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REMEDIAL ACTION CONTRACT
United States Environmental Protection Agency Region 6
Contract No. EP-W-06-021
Annual Groundwater Sampling Report for 2014 EPA Final
Fruit Avenue Plume Superfund Site
Albuquerque, New Mexico Remedial Action Contract No. EP-W-06-021
Task Order Number 0003-RALR-06DD Document Control Number 0003-02112
January 2015
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FRUIT AVENUE PLUME SUPERFUND SITE ANNUAL GROUNDWATER SAMPLING REPORT FOR 2014
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F ina l Repo r t
Fruit Avenue Plume Superfund Site Annual Groundwater Sampling
Report for 2014
Prepared for
U.S. Environmental Protection Agency
January 2015
Contract No. EP‐W‐06‐021
Task Order No. 0003‐RALR‐06DD CH2M HILL Project No. 345406
Document Control No. 0003‐02112
12750 Merit Drive
Suite 1100 Dallas, Texas 75251
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FRUIT AVENUE PLUME SUPERFUND SITE ANNUAL GROUNDWATER SAMPLING REPORT FOR 2014
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Executive Summary This report summarizes the findings from the two groundwater monitoring events conducted in February and August 2014 as part of the long‐term remedial action underway at the Fruit Avenue Plume (FAP) Superfund Site (site), located in downtown Albuquerque, New Mexico. The purpose of the monitoring events, and this report, is to evaluate groundwater elevation and flow patterns, and trichloroethene (TCE) concentration trends in groundwater, to assess the overall effectiveness of the remedial action. The remediation goals for volatile organic compounds (VOC) present in groundwater at the site are: tetrachloroethene (PCE), 5 micrograms per liter (µg/L); TCE, 5 µg/L; cis‐1,2‐dichloroethene (cis‐1,2‐DCE), 70 µg/L; and trans‐1,2‐dichloroethene (trans‐1,2‐DCE), 100 µg/L (U.S. Environmental Protection Agency [EPA], 2001).
Groundwater sampling activities were completed in accordance with the EPA‐approved Sampling and Analysis Plan (SAP), which consists of the Field Sampling Plan (FSP) (CH2M HILL, 2010a), the Quality Assurance Project Plan (QAPP; CH2M HILL, 2010b), and the SAP Version 2.1 – Addendum No. 1 (CH2M HILL, 2010c) as modified by the Monitor Well Abandonment Rationale technical memorandum (CH2M HILL, 2010d) and the Annual Groundwater Sampling Report for 2011 (CH2M HILL, 2012a).
Sampling of the semiannual and annual long‐term monitoring (LTM) wells occurred during the February 2014 event, and sampling of the semiannual LTM wells occurred during the August 2014 event.
Groundwater Elevation and Flow The groundwater elevation contour and flow maps continue to show consistent groundwater flow directions in each of the six aquifer zones monitored at the site.1 Except in the far western portion of the site, where the groundwater flow direction is to the east‐northeast, groundwater flows generally toward the east or east‐southeast in each aquifer zone. Groundwater elevations continue to fluctuate seasonally, generally rising during the winter months and falling during the late spring through summer months, when pumping from the public water supply wells located to the east of the site is greatest. Superimposed over the seasonal, cyclic fluctuations, is an overall upward trend. Site‐wide groundwater elevations have increased between 1 and 26 feet since 2004, as a larger fraction of the local water supply is obtained from surface water versus groundwater resources.
Water level measurements were obtained on February 16 and August 24, 2014. The pump‐and‐treat (P&T) system has been turned off since May 20, 2013, following its transition to standby mode. The long‐term influence of groundwater pumping at extraction well D2E‐P1 is evident in the groundwater elevation contour and flow maps for the D1, D2, D3, and D4 aquifer zones.
TCE Distribution and Concentration Trends The distribution of TCE in site groundwater is generally consistent with that observed during prior monitoring events. The highest observed concentrations of TCE continue to occur in the I2 aquifer zone, near the site’s presumed source area. TCE concentrations observed during the August 2014 event ranged from less than 0.5 µg/L to 44.8 µg/L. The highest concentration (44.8 µg/L) was detected at monitor well MNW‐14 (I2), which is located just south‐southwest (cross‐gradient) from the presumed source area, a location potentially in the path of TCE migration associated with the up‐gradient offsite plume. TCE concentrations in the I2 aquifer zone monitor well HSM‐I2‐5, also located near the presumed source area,
1 See sampling and analysis plan (CH2M HILL, 2010a) for discussion of site hydrogeology and aquifer zone designations. Aquifer Zone Designations: S = Shallow, I1 = Intermediate Zone 1, I2 = Intermediate Zone 2, D1 = Deep Zone 1, D2 = Deep Zone 2, D3 = Deep Zone 3, D4 = Deep Zone 4
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EXECUTIVE SUMMARY
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continued to decrease from the historical high of 99 µg/L, which was observed in April 2005, to 26 µg/L in August 2014.
The TCE concentrations at monitor well MNW‐5, located east (downgradient) of the P&T system extraction well, continue to fluctuate in the D1 and D2 aquifer zones, while decreasing in the deeper D3 zone. TCE concentrations at MNW‐5 (D3) (16.4 μg/L) have been decreasing steadily since August 2011 (27 µg/L). New monitor wells MNW‐16 (D1, D2, D3, and D4), which were installed in April 2012 on the eastern side of Interstate Highway 25, have been sampled semiannually since they were installed; TCE has not been detected above the 0.5‐µg/L reporting limit in any of the samples collected from the different aquifer zones.
Recommendations Based on information presented in the Final Monitored Natural Attenuation Report (CH2M HILL, 2013a), EPA is considering modifying the groundwater remedy to expand monitored natural attenuation (MNA) to include the central and western portions of the FAP site TCE plume. Concurrent with this potential modification, the P&T system has been placed in standby mode after meeting the criteria established in the remedial system evaluation (CH2M HILL, 2009b), while monthly performance sampling, and LTM program groundwater monitoring and reporting continue per the current schedule. While in standby mode, samples of the air stripper treatment plant (ASTP) influent will continue to be collected during quarterly performance monitoring events to demonstrate the operability of the ASTP. The collection of effluent samples is considered to be unnecessary because of the long history of documented system effectiveness, and therefore it is recommended that these samples be excluded from future sampling events. Continued monitoring of the system’s functionality (blower operation and tray status) can be performed as part of quarterly inspections.
The current groundwater monitoring network and sampling schedule is sufficient to develop the information needed to confirm that the remedy modification under consideration is protective of human health and the environment. Some additional MNA‐specific sampling was recommended by the Final Monitored Natural Attenuation Report (CH2M HILL, 2013a), Therefore, groundwater monitoring, in accordance with the FSP and LTMO, should continue; and an addendum to the FSP will be issued to direct the next MNA sampling event, which is expected to be conducted in February 2015.
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Contents
Section Page
Executive Summary ............................................................................................................................... ES-1
Contents ...................................................................................................................................................... i
1 Introduction ................................................................................................................................ 1-1
2 Description of Field Activities ...................................................................................................... 2-1 2.1 Water Level Collection Activities .......................................................................................... 2-1 2.2 Groundwater Sampling Activities ......................................................................................... 2-1
2.2.1 Groundwater Sample Collection .............................................................................. 2-2 2.2.2 Air Stripper Treatment Plant Performance Sample Collection................................. 2-2 2.2.3 Monitor Wells New to the LTM Program ................................................................. 2-2
3 Description of Results .................................................................................................................. 3-1 3.1 Water Level Distribution ....................................................................................................... 3-1
3.1.1 Horizontal Groundwater Flow ................................................................................. 3-1 3.1.2 Vertical Groundwater Flow ...................................................................................... 3-2 3.1.3 Groundwater Elevation Trends between February 2002 and August 2014 ............. 3-2
3.2 Description of Analytical Results ........................................................................................... 3-3 3.2.1 Summary of August 2014 Results ............................................................................ 3-3 3.2.2 TCE Concentration Trends between February 2002 and August 2014 .................... 3-4
3.3 ASTP Performance Sampling Results .................................................................................... 3-5
4 Conclusions ................................................................................................................................. 4-1 4.1 Groundwater Flow ................................................................................................................ 4-1 4.2 Distribution of Chlorinated Solvents ..................................................................................... 4-1 4.3 Contaminant Concentration Trends in Groundwater ........................................................... 4-2
5 Recommendations ...................................................................................................................... 5-1
6 Works Cited ................................................................................................................................. 6-1
Tables
2-1 Monitor Well and PDB Installation Details 2-2 Planned Sampling Frequency for Site Wells 2-3 Water Level Measurements, August 24, 2014 3-1 Horizontal Groundwater Flow Gradients between Selected Monitor Wells for Each Aquifer Zone 3-2 Vertical Groundwater Flow Direction at Selected Monitor Well Locations 3-3 Summary of Historical Groundwater Elevation, February 2002 through August 2014 3-4 Summary of Chlorinated VOCs Detected in Groundwater, August 25, 2014 3-5 Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through
August 2014 3-6 Summary of Analytical Results from Recent ASTP Influent Water Sampling
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CONTENTS
Figures
2-1 Site Map, August 2014 3-1 Distribution of Water Levels in the Shallow Aquifer Zone, August 2014 3-2 Distribution of Water Levels in the I1 Aquifer Zone, August 2014 3-3 Distribution of Water Levels in the I2 Aquifer Zone, August 2014 3-4 Distribution of Water Levels in the D1 Aquifer Zone, August 2014 3-5 Distribution of Water Levels in the D2 Aquifer Zone, August 2014 3-6 Distribution of Water Levels in the D3 Aquifer Zone, August 2014 3-7 Distribution of Water Levels in the D4 Aquifer Zone, August 2014 3-8 Shallow Aquifer Zone - Groundwater Elevation Trends over Time, February 2002 through August
2014 3-9 I1 Aquifer Zone – Groundwater Elevation Trends over Time, February 2002 through August 2014 3-10 I2 Aquifer Zone – Groundwater Elevation Trends over Time, February 2002 through August 2014 3-11 D1 Aquifer Zone – Groundwater Elevation Trends over Time, February 2002 through August
2014 3-12 D2 Aquifer Zone - Groundwater Elevation Trends over Time, February 2002 through August 2014 3-13 D3 Aquifer Zone - Groundwater Elevation Trends over Time, February 2002 through August 2014 3-14 D4 Aquifer Zone - Groundwater Elevation Trends over Time, February 2002 through August 2014 3-15 Distribution of Chlorinated Solvents in the I1 Aquifer Zone August 2014 3-16 Distribution of Chlorinated Solvents in the I2 Aquifer Zone, August 2014 3-17 Distribution of Chlorinated Solvents in the D1 Aquifer Zone, August 2014 3-18 Distribution of Chlorinated Solvents in the D2 Aquifer Zone, August 2014 3-19 Distribution of Chlorinated Solvents in the D3 Aquifer Zone, August 2014 3-20 Distribution of Chlorinated Solvents in the D4 Aquifer Zone, August 2014 3-21 I1 Aquifer Zone- TCE Concentration Trends Over Time, November 1997 through August 2014 3-22 I2 Aquifer Zone - TCE Concentration Trends Over Time April 1997 through August 2014 3-23 D1 Aquifer Zone - TCE Concentration Trends Over Time, October 1997 through August 2014 3-24 D2 Aquifer Zone - TCE Concentration Trends Over Time, November 1997 through August 2014 3-25 D3 Aquifer Zone - TCE Concentration Trends Over Time, July 1998 through August 2014 3-26 Upgradient Offsite Plume – I2 and D1 Aquifer Zones - TCE Concentration Trends over Time, April
2005 through August 2014 3-27 TCE Concentration in Untreated Influent Groundwater, January 2005 through August 2014
Appendixes
A Fruit Avenue Plume Superfund Site Summary of the First Semiannual Groundwater Sampling Event for 2014
B CLP Traffic Reports C VOC Analytical Data Summary Tables
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Acronyms and Abbreviations µg/L microgram per liter
ABCWUA Albuquerque Bernalillo County Water Utility Authority
ASTM ASTM International (formerly American Society for Testing and Materials)
ASTP air stripper treatment plant
BNSF Burlington Northern Santa Fe
cis-1,2-DCE cis-1,2-dichloroethene
CLP Contract Laboratory Program
D1 Deep-1 aquifer zone
D2 Deep-2 aquifer zone
D3 Deep-3 aquifer zone
D4 Deep-4 aquifer zone
EPA U.S. Environmental Protection Agency
ESAT Environmental Services Assistance Team
FAP Fruit Avenue Plume
FSP field sampling plan
ft/ft foot per foot
I1 Intermediate-1 aquifer zone
I2 Intermediate-2 aquifer zone
LTM long-term monitoring
LTMO long-term monitoring optimization
MCL maximum contaminant level
ml milliliter
MNA monitored natural attenuation
NMED New Mexico Environment Department
P&T pump and treat
PCE perchloroethene (tetrachloroethene)
PDB passive diffusion bag
QAPP quality assurance project plan
QC quality control
S shallow aquifer zone
SAP sampling and analysis plan
site Fruit Avenue Plume Superfund Site
TCE trichloroethene
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ACRONYMS AND ABBREVIATIONS
TCL target compound list
TM technical memorandum
trans-1,2-DCE trans-1,2-dichloroethene
UNM University of New Mexico
USGS United States Geological Survey
VC vinyl chloride
VOA volatile organic analysis
VOC volatile organic compound
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SECTION 1
Introduction This report summarizes the results from two semiannual groundwater sampling events conducted in February and August 2014 at the Fruit Avenue Plume (FAP) Superfund Site (site) located in Albuquerque, New Mexico. The sampling was performed in accordance with the site Sampling and Analysis Plan (SAP), which consists of the Field Sampling Plan (FSP) (CH2M HILL, 2010a) and the Quality Assurance Project Plan (QAPP) (CH2M HILL, 2010b), as well as the SAP Version 2.1 – Addendum No. 1 (CH2M HILL, 2010c), as modified by the Monitor Well Abandonment Rationale technical memorandum (TM) (CH2M HILL, 2010d) and the Annual Groundwater Sampling Report for 2011 (CH2M HILL, 2012). Both sampling events included the measurement of water levels from all accessible site monitor wells and the collection of groundwater samples from a subset of the site monitor wells.
Groundwater monitoring is conducted at the site to assess volatile organic compound (VOC) (specifically, trichloroethene [TCE]) concentration trends, plume migration, and performance of the groundwater remedy as described in the Record of Decision, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico (U.S. Environmental Protection Agency [EPA], 2001) and Explanation of Significant Differences, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico (EPA, 2006).
The information presented in this report focuses primarily on the August 2014 monitoring results. The February 2014 monitoring results were presented in Summary of the First Semiannual Groundwater Sampling Event for 2014: Fruit Avenue Plume Superfund Site (CH2M HILL, 2014a), which is included as Appendix A. That report provided very little data evaluation and assessment of TCE distribution and concentration trends at the site. This report summarizes the data collected during the August 2014 groundwater monitoring event and presents an evaluation of long-term groundwater elevation and TCE concentration trends based on new and historical data.
There is an off-site upgradient chlorinated solvent plume west of, and merging with, the FAP (CH2M HILL, 2013a). Historical results indicate that, near the western boundary of the FAP site, the off-site upgradient plume is limited to the I2 and D1 aquifer zones. Groundwater samples and water levels were collected from monitor wells that are associated with that plume, and the results were tabulated and charted. A limited discussion is included to evaluate potential effects upon the FAP.
This report is organized into six sections. Section 1 is the introduction. Section 2 provides a summary of the field activities. Section 3 discusses the results of the sampling events. Section 4 provides conclusions. Section 5 offers recommendations. Section 6 presents works cited in this report.
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Description of Field Activities Groundwater monitoring activities for the February and August 2014 sampling events were conducted by CH2M HILL and New Mexico Environment Department (NMED) staff. Field activities included collection of 40 groundwater samples (plus 4 quality control [QC] samples) from 28 monitor wells, using passive diffusion bag (PDB) samplers. Table 2‐12 lists the wells sampled, while Figure 2‐13 presents a map showing their locations. Water level measurements were collected during both sampling events.
Site monitor wells are sampled on a schedule first recommended in the LTMO (CH2M HILL, 2009a), codified in the SAP Version 2.1 – Addendum No. 1 (CH2M HILL, 2010c), and modified based on recommendations made in the Annual GW Monitoring Reports for 2011 (CH2M HILL, 2012), 2012 (CH2M HILL, 2013c), and 2013 (CH2M HILL, 2014b). Table 2‐2 presents the current sampling schedule. The semiannual list is sampled during both the winter and summer sample events. Monitor wells on the annual list are sampled only during the the winter event. Monitor wells on the biennial list are sampled during the winter event only on odd‐numbered years. The semiannual and annual long‐term monitoring (LTM) wells were sampled during the February 2014 sampling event; and the semiannual LTM wells were sampled during the August 2014 sampling event.
The P&T system has been turned off since May 20, 2013, following its transition to standby mode based on recommendations provided in Cleanup Status Report No. 40 (CH2M HILL, 2013b).
2.1 Water Level Collection Activities On August 24, 2014, prior to groundwater sampling, water level measurements were collected from 103 site monitor wells (Table 2‐3).
2.2 Groundwater Sampling Activities The LTM program at the site consists of groundwater sampling using PDBs. Multiple PDBs, typically three or four, are installed in each monitor well along the screen interval to assess the potential for VOC stratification in the well. The number of PDBs and depth of installation in each well depend on the length of the well screen.
In preparation for the February 2014 groundwater sampling event, the PDBs that are sampled as part of the LTM program were replaced. The PDB replacement was done to guard against unnoticed biofouling and to prevent inadvertent sampling of the wrong PDB. The PDBs that are not part of the LTM program were removed, and their associated weights and tethers were stored in the monitor wells for future use. The PDBs were replaced on January 26, 2014, which allowed more than the manufacturer‐recommended 2 weeks for organic‐free water placed in the PDBs to equilibrate with the groundwater.
During this sampling event, selected PDBs were sampled in most wells based on recommendations provided in the long‐term monitoring optimization (LTMO) report (CH2M HILL, 2009a), and as implemented by FSP Version 2.1 (CH2M HILL, 2010a) and SAP Version 2.1 – Addendum No. 1 (CH2M HILL, 2010c). The total number of PDB intervals sampled at a given well was determined based on TCE concentrations observed during previous sampling events. Using this information, the PDB or PDBs with the maximum observed TCE concentration in each well are generally sampled. If all previous PDB samples from a single well indicated
2 Tables are located at the end of this report, behind the Tables divider.
3 Figures are located at the end of this report, behind the Figures divider.
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non‐detect values, then a single PDB interval was selected as being representative for the entire well screen length. The PDB intervals sampled during the August 2014 event are shown in Table 2‐1.
Groundwater samples and water levels are collected from monitor wells that are associated with the off‐site upgradient plume, and the results are included in the subsequent table, charts, and maps (such as Figure 2‐1). Limited discussion is included in this report to evaluate potential effects on the FAP.
2.2.1 Groundwater Sample Collection Groundwater sampling activities were initiated on August 24, 2014, and completed on August 25, 2014. While sampling at each location, the PDBs were removed from the well and placed on plastic sheeting to prevent contact with the ground. A VOC sample was collected by pouring water from the PDB directly into 40‐milliliter (ml) volatile organic analysis (VOA) containers with septa‐lined caps. After sample collection, each PDB was inspected; if it was in good condition, it was retained for reuse. The empty PDBs were refilled with ASTM International (ASTM [formerly known as American Society for Testing and Materials]) Type II water, prior to lowering the tether and the attached PDBs back into the well for the next groundwater sampling event. Most PDBs have been in place in each monitor well since the conclusion of the previous sampling event in February 2014. While PDB vendors recommend discarding the PDBs after each use, the PDBs at this site are reused as long as structural integrity is maintained and no biofilm is observed on the surface of the PDB. A PDB is changed if either condition occurs.
Groundwater samples were submitted to the Houston EPA Laboratory for VOC analysis and reporting of compounds identified on the target compound list (TCL). The TCL includes the chlorinated solvents tetrachloroethene (PCE); TCE; cis‐1,2‐dichloroethene (cis‐1,2‐DCE) and trans‐dichloroethene (trans‐1,2‐DCE); and vinyl chloride (VC). Samples were shipped overnight, from the field to the laboratory, on the date of sample collection.
2.2.2 Air Stripper Treatment Plant Performance Sample Collection Routine sampling of the air stripper treatment plant (ASTP) untreated influent groundwater and treated effluent was conducted approximately quarterly. The ASTP was operated for approximately 2 hours to purge approximately 5,400 gallons from the well and associated pipelines. Grab samples were collected from the ASTP influent (sample port SP‐1) and effluent (sample port SP‐5) sample ports. Like LTM groundwater samples, ASTP performance samples were submitted to the Houston EPA Laboratory for VOC analysis and reporting of compounds identified on the TCL.
2.2.3 Monitor Wells New to the LTM Program During the February 2014 event, monitor wells new to the LTM program (including nest MNW‐16 [D1, D2, D3, D4]) and McDonalds (D2) were sampled. The laboratory analysis results were reviewed to evaluate for potential vertical TCE stratification across the screened interval; the PDBs that were deemed most representative were selected.
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Description of Results This section provides the water level measurements and VOC concentration results from the August 2014 semiannual groundwater monitoring event. Water level measurement data and contaminant concentration results from the February 2014 semiannual groundwater monitoring event are provided in Appendix A.
3.1 Water Level Distribution The August 2014 water level measurements are provided in Table 2-3. Based on these data, Figures 3-1 through 3-7 illustrate the distribution of water levels in the shallow (S), intermediate-1 (I1), intermediate-2 (I2), deep-1 (D1), deep-2 (D2), deep-3 (D3), and deep-4 (D4) aquifer zones. Hydrographs of historical groundwater elevation trends, measured during each groundwater sampling event since February 2002, are presented in Figures 3-8 through 3-14.
3.1.1 Horizontal Groundwater Flow In general, groundwater flow at the site in each aquifer zone is from west to east, toward the University of New Mexico (UNM) and the Albuquerque Bernalillo County Water Utility Authority (ABCWUA) groundwater production wellfields, located south-southeast of the site. In the S, I1, and I2 aquifer zones, the groundwater flow direction is toward the east-northeast (Figures 3-1, 3-2, and 3-3, respectively) in the western portion of the site, transitioning to an easterly direction near the railroad tracks. In the D1, D2, and D3 aquifer zones (Figures 3-4, 3-5, and 3-6, respectively), the predominant groundwater flow direction is generally toward the east in the western portion of the site, and toward the east-southeast in the eastern portion of the site. In the D4 aquifer zone, the groundwater flow direction is generally toward the southeast (Figure 3-7) in the area outside the influence of the pump-and-treat (P&T) system extraction well.
As part of the site remedy, contaminated groundwater was extracted from the aquifer, treated in the ASTP to remove VOCs, and re-injected to the aquifer. The single extraction well is screened in the D2 aquifer zone and located near the intersection of Arno Street and Roma Avenue (Figure 2-1). Treated water was re-injected at two locations: one single-screen well, which is screened in the D2 aquifer zone and is located near the intersection of Roma Avenue and St. John Street; and a dual-screen well, which is screened in the I2 and D1 aquifer zones and is located on Commercial Street between Roma Avenue and Marquette Avenue. Although the P&T system has been in standby mode (shut down) since May 2013, the hydraulic effect of the P&T system is still apparent near the extraction well on the D1, D2, D3, and D4 aquifer zone groundwater elevation contour and flow maps (Figures 3-4 through 3-7).
The groundwater flow direction in each aquifer zone is generally consistent with the flow directions observed in previous monitoring events, including the area near the extraction well.
The horizontal groundwater flow gradients from previous sampling events are presented in Table 3-1. During the August 2014 monitoring event, horizontal groundwater flow gradients ranged from 0.0003 foot per foot (ft/ft) in the D4 aquifer zone (SMFW-34 to MNW-7), up to 0.0158 ft/ft in the I2 aquifer zone (SFMW-21 to SFMW-31). The horizontal flow gradients are generally lower in the western and far eastern portions of the site, gradually increasing in the central area of the site near the Burlington Northern Santa Fe (BNSF) railroad tracks and the P&T system. The highest observed horizontal flow gradients occur in the I1, I2, D1, and D2 aquifer zones, near the BNSF railroad tracks. It is suspected that a fault or other geologic barrier located in this area inhibits groundwater flow, resulting in higher horizontal flow gradients. Horizontal flow gradients in the western portion of the site have been decreasing with time, in concert with increasing water levels.
The horizontal groundwater flow gradients have generally remained consistent since regular monitoring began at the site in November 2004, with the exception of localized areas near the P&T system, where the
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direction and magnitude of groundwater flow have changed under the influence of the extraction and injection wells associated with P&T system operations. The groundwater elevation data show that the cone of depression formed in the D1, D2, D3, and D4 aquifer zones around extraction well D2E-P1 had not fully subsided at the time of the August 2014 sampling event, approximately 15 months after the P&T system was placed in standby mode.
3.1.2 Vertical Groundwater Flow Vertical groundwater flow directions were evaluated at 11 locations where 2 or more monitor wells, completed in different aquifer zones, are located close to one another. Table 3-2 presents the vertical groundwater flow direction for these nine well pairs.
In the western (presumed source area) and eastern (eastern site boundary) portions of the site, the differences in water level elevations between adjacent aquifer zones are generally less than 2 feet. Vertical groundwater flow gradients in these areas of the site are very small. An exception to this occurs in the vicinity of monitor well MNW-15, which is located in the eastern site boundary area. At this location, the vertical flow gradient is upward, with a maximum observed difference in water level elevations of -10.1 feet, observed between the D1 and D3 aquifer zones during the August 2014 groundwater monitoring event. The upward flow direction is possibly associated with pumping at the production wells to the east, UNM #7 and Presbyterian Hospital, which are believed to be screened across the D1, D2, and D3 aquifer zones.
Differences in water level elevations, in terms of vertical groundwater flow, can be divided into three distinct geographic zones, depending on the proximity of the zone to the presumed fault and extraction well D2E-P1, as follows:
• Presumed Source Area (Western Portion of Site). In the area upgradient of the presumed fault zone (at the DM-13, SFMW-07/SFMW-18/MNW-14, and SFMW-15/SFMW-16/SFMW-17 well groups), the vertical groundwater flow direction has generally been upward.
• Central Plume Area. In this area, located just east of the presumed fault zone, the vertical groundwater flow direction continues to be generally downward. At the SFMW-33/SFMW-34 well pair (located next to the railroad tracks), the difference in water level elevations between the D2 and D4 aquifer zones was +4.07 feet. Water levels at the SFMW-20 and SFMW-32 monitor well groups also continue to indicate generally downward flow in the D1 to D4 aquifer zones, and show the effects of extraction well pumping. The difference in water level elevations between the I2 and D4 aquifer zones during the August 2014 event was +2.47 feet at the SFMW-20/SFMW-21/SFMW-22/SFMW-23/SFMW-35/SFMW-36 well group.
• Eastern Site Boundary. At the eastern site boundary, the vertical groundwater flow direction continues to be upward. At the MNW-15 D1/D2/D3 well group, the difference in water level elevations between the D1 and D3 aquifer zones was -10.1 feet.
3.1.3 Groundwater Elevation Trends between February 2002 and August 2014
Groundwater elevation measurements, taken at a subset of monitor wells since February 2002, are presented in Table 3-3. These data were used to prepare the hydrographs that show groundwater elevation trends over time in each aquifer zone, presented graphically in Figures 3-8 through 3-14 for the S, I1, I2, D1, D2, D3, and D4 aquifer zones, respectively.
Groundwater elevations are generally stable or rising over the period of the site-specific measurements. A decrease in water levels caused by pumping of the aquifer by regional production wells is discernible in the early data, and a water level increase is evident in the more recent data in response to reductions in municipal groundwater pumping. As the San Juan-Chama (surface water) diversion project came online, the ABCWUA has begun reducing the volume of groundwater entering the water supply system. However,
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ABCWUA wells are still in use to augment the surface water source and allow for blending to control arsenic concentrations. In response, water levels are expected to continue rising across the site, from 5 to 25 feet over the next 30 years (United States Geological Survey [USGS], 2003). The potential effects of rising groundwater elevations in the D1, D2, D3, and D4 aquifer zones on TCE plume migration are reflected in the flow-and-transport modeling results reported in the Final Monitored Natural Attenuation Report (CH2M HILL, 2013a).
Groundwater elevations in all aquifer zones fluctuate seasonally, generally varying less than 10 feet. During the summer months, the ABCWUA supply wells pump at higher rates as water use increases in the City of Albuquerque. Groundwater elevations fluctuate very little to the west of the site. Seasonal fluctuations are less pronounced in the S, I1, and I2 aquifer zones (Figures 3-8, 3-9, and 3-10, respectively). However, in the deep aquifer zones, greater seasonal variations are evident between spring and fall groundwater elevation periods (Figures 3-11, 3-12, 3-13, and 3-14, respectively). These differences are most likely attributed to seasonal groundwater pumping at the UNM and ABCWUA supply wells.
3.2 Description of Analytical Results A summary of the chlorinated VOC (TCE, PCE, cis-1,2-DCE, trans-1,2-DCE, and VC) results for the August 2014 event is provided in Table 3-4. Table 3-5 summarizes the chlorinated VOC results from 1997 through August 2014. Appendix B contains the traffic reports for the groundwater samples submitted to the Contract Laboratory Program (CLP) laboratory. The original laboratory report for samples sent to the CLP laboratory are stored by EPA and referenced as Case Number 1408020. Appendix C presents all the VOC results for groundwater samples collected during the August 2014 groundwater sampling event. A discussion of the results is presented in Section 3.2.1.
The VOC data were validated by EPA in accordance with National Functional Guidelines by the Environmental Services Assistance Team (ESAT) prior to delivery to CH2M HILL. All data were found to be suitable for use in this report.
3.2.1 Summary of August 2014 Results The August 2014 groundwater samples had detections of several VOCs, including: TCE, cis-1,2-DCE, trans-1,2-DCE, VC, and PCE. TCE was the only VOC detected at concentrations exceeding its remedial goal of 5 micrograms per liter (µg/L). The range of concentrations observed includes:
• TCE concentrations ranged from less than 0.5 µg/L to 44.8 µg/L, with the highest observed concentration detected at MNW-14 (I2). TCE concentrations greater than the 5 µg/L remediation goal were detected in 20 of 36 (56 percent) PDB samples that were collected in August 2014. (Note: This count does not include field duplicates).
• Cis-1,2-DCE concentrations ranged from less than 0.5 µg/L to a highest-observed concentration of 9.9 µg/L (MNW-5 [D3]). Cis 1,2-DCE was not detected in any of the samples at concentrations above its 70 µg/L remediation goal.
• Trans-1,2-DCE concentrations ranged from less than 0.5 µg/L to a highest-observed concentration of 6.4 µg/L (MNW-5 [D3]). Trans 1,2-DCE was not detected in any of the samples at concentrations above its 100 µg/L remediation goal.
• VC was not detected during this sampling event. The record of decision did not establish a remediation goal for VC. While the primary drinking water standard (maximum contaminant level [MCL]) for VC is 2 µg/L, the State of New Mexico has established a maximum concentration of 1 µg/L (New Mexico Administrative Code 20.6.2.3103) in groundwater that is a current or potential drinking water source.
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• PCE concentrations ranged from less than 0.5 µg/L to 1.4 µg/L, with the highest-observed concentration detected at MNW-5 (D1). PCE was not detected in any of the samples at concentrations above its 5 µg/L remediation goal.
Based on the August 2014 analytical results, Figures 3-15 through 3-20 were prepared to show the concentration of chlorinated solvents and distribution of TCE detected in the I1, I2, D1, D2, D3, and D4 aquifer zones, respectively. Because samples were collected from multiple PDBs at some well locations, the highest detected result for each chlorinated solvent in each aquifer zone at each well is presented on these figures. Concentration contours for TCE (1, 5, 10, and 20 µg/L, as applicable) are also provided on the figures. Based on the analytical results and data presented on the figures, the following observations can be made from these figures regarding TCE distribution in groundwater at the site:
• The perimeter of the TCE plume in each aquifer zone is generally well defined within the site boundary to concentrations below the remediation goal of 5 µg/L.
• The highest-observed TCE concentration in the I1 aquifer zone was 25.2 µg/L, at monitor well SFMW-47 (I1/I2) (Figure 3-15).
• The highest site-related TCE concentration in the I2 aquifer zone monitor wells sampled was 44.8 µg/L, at monitor well MNW-14 (I2) (Figure 3-16).
• The highest site-related TCE concentration observed in the D1 aquifer zone monitor wells sampled was 9.7 µg/L, at monitor well MNW-5 (D1) (Figure 3-17).
• The highest-observed TCE concentration in the D2 aquifer zone monitor wells sampled was 14.9 µg/L, at monitor well MNW-5 (D2) (Figure 3-18).
• The highest-observed TCE concentration in the D3 aquifer zone monitor wells sampled was 16.4 µg/L, at monitor well MNW-5 (D3) (Figure 3-19).
• During the August 2014 sampling event, TCE was detected at 0.6 µg/L at SFMW-41 (D3 and D4), which is screened between the D3 and D4 aquifer zones (Figure 3-20). TCE has not been detected at concentrations exceeding the remedial goal in this well or in any other D4 aquifer zone wells.
Sample results from the western end of the site continue to indicate the presence of an upgradient offsite TCE plume (Figure 2-1). The highest observed TCE concentration, detected in samples collected from monitor wells used only to track the offsite plume, was 29.0 µg/L (MNW-11 [I2]). During future sampling events, groundwater samples will continue to be collected from selected upgradient monitor wells to track this plume’s migration and potential impacts on the FAP remedial action.
3.2.2 TCE Concentration Trends between February 2002 and August 2014 The chlorinated solvent results for samples collected at the site since 1986 are provided in Table 3-5. These data were used to prepare graphs that show TCE concentration trends over time, in each of the aquifer zones where TCE has consistently been detected above a concentration of 1 µg/L. These graphs are presented in Figures 3-21 through 3-25 for the I1, I2, D1, D2, and D3 aquifer zones. For each sampling event, where multiple PDB samples were collected from a single monitor well, the highest TCE concentration is presented on the graph. Where a well is screened across two aquifer zones, analytical results from each aquifer zone are posted on separate graphs. Graphs were not prepared for the S and D4 aquifer zones because of the lack of monitor wells where TCE is consistently detected above 1 µg/L. In general, the TCE concentrations at a majority of the site monitor wells are decreasing or stable. Exceptions to this general trend occur at MNW-5 (D1, D2, and D3) and MNW-14 (I2).
Monitor well MNW-5 is used to track the downgradient portion of the TCE plume. After declining from 18 µg/L to 4.1 µg/L between 2004 and August 2010, TCE concentrations at MNW-5 (D1) have increased, rising from 4.1 µg/L to 9.7 µg/L in August 2014 (Figures 3-23). TCE concentration trends at MNW-5 (D2) were similar to those of MNW-5 (D1), with concentrations declining from 22 µg/L to 8.6 µg/L between 2004
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and February 2011, rising to 14.9 µg/L in August 2014 (Figure 3-24). The TCE concentrations measured at MNW-5 (D3) generally increased following installation of this well in 2004 (Figure 3-25). In 2011, concentrations began to decrease, from 27 µg/L in August 2011 to 16.4 µg/L in August 2014.
At the downgradient leading edge of the plume, the TCE concentrations measured at MNW-4(D2), while below the 5 µg/L remedial goal, are increasing.
Closer to the P&T system, the August 2014 TCE concentration in the McDonalds (D2) well (6.3 µg/L) confirms a decreasing concentration trend since February 2011, when concentrations peaked at 11 µg/L. At SFMW- 23(D2), which is located between the D2 injection well and the extraction well and which demonstrated break-through of treated water within months of system startup, TCE concentrations have increased from 1.7 µg/L in February 2013, before the ASTP was placed in standby mode, to 10.6 µg/L in August 2014 (Figure 3-24).
MNW-14 (I2) is near the presumed source area. This well was installed to replace SFMW-19 (I2), which had consistently shown the highest TCE concentrations at the site, but had become unusable. The TCE concentration measured in MNW-14 (I2) (44.2 µg/L, shown on Figures 3-16 and 3-22) during the August 2014 event continues to be among the highest observed at the site.
TCE concentrations at the upgradient offsite plume continue to fluctuate (Figure 3-26), except at well MNW-9 (I2), which shows a consistent decreasing trend, and MNW-1 (I2) and MNW-11 (D1), which show an increasing trend. Compared to the August 2013 plume boundaries (Figure 3-17 in Annual Groundwater Sampling Report for 2013 [CH2M HILL, 2014b]), the leading edge of the upgradient offsite plume in the D1 aquifer zone has moved to the east and now lies within the FAP site boundary.
3.3 ASTP Performance Sampling Results VOC concentrations in the ASTP influent (sample port SP-1) and effluent (sample port SP-5), for the period from the September 2013 through August 2014, are summarized in Table 3-6. TCE concentrations in the untreated ASTP influent observed since 2005 are illustrated in Figure 3-27. Over the past 12 months, TCE concentrations in the ASTP influent ranged from a high of 3.6 μg/L in September 2013 to a low of 2.4 μg/L in February 2014. TCE concentrations in the ASTP influent samples were equal to or less than the 5 μg/L remediation goal in all of the past year’s samples. Contaminants have not been detected in ASTP effluent samples, demonstrating the effectiveness of the treatment plant for removing site contaminants from the process flow.
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Conclusions Conclusions based on the data obtained during the February and August 2014 monitoring events are presented in this section.
4.1 Groundwater Flow The groundwater elevation contour maps (Figures 3-1 through 3-7) continue to show consistent groundwater flow directions at the site. Except within the far western portion of the site, where the direction of groundwater flow is east-northeast, groundwater flows generally toward the east, varying between an east-northeast and east-southeast direction in each aquifer zone. The greater horizontal and vertical flow gradients observed in the central portion of the site, near the railroad tracks, continue to support the interpretation that a geologic barrier to groundwater flow, suspected to be a fault, occurs in this area.
Groundwater flow patterns observed near the P&T system in August 2014 indicate a semi-convergent flow pattern in the D1, D2, D3, and D4 aquifer zones, even though the P&T system was placed in a pulsed-off mode in May 2013. The slow decay of the P&T system’s hydraulic capture zone is consistent with observations made during other post-shutdown events.
Groundwater elevations fluctuate seasonally in each of the aquifer zones, in response to natural variations in recharge (rainfall and snowmelt infiltration) and withdrawal (water supply pumping). Groundwater elevation changes do not vary significantly in the S, I1, and I2 aquifer zones (Figures 3-8 through 3-10). Seasonal groundwater elevation variations are more prominent in the D1 through D4 aquifer zones, with D4 groundwater elevations showing the greatest fluctuation (Figures 3-11 through 3-14). The increasing water levels at MNW-15 (D2 and D3) may be an indicator of a change in the flow regime, which could lead to the plume shifting toward the south-southeast in the future. Increased reliance on surface water resources, as part of the San Juan-Chama project, is expected to cause groundwater elevations in the presumed source area to rise, which have the potential to mobilize sorbed contaminants that may be present in the capillary fringe portion of the shallow aquifer zone. Evidence of rising groundwater elevations in aquifer zones S, I1, and I2 is already present at many monitor well locations (that is, DM-01 [S], DM-05 [S], DM-13 [S, I1, I2], and SFMW-03; see Table 3-3). At this time, in these areas, there have been no observed increases in contaminant concentrations that are attributable to increasing water levels.
4.2 Distribution of Chlorinated Solvents TCE, cis-1,2-DCE, trans-1,2-DCE, and PCE were detected in the 2014 groundwater samples. TCE concentrations exceeded the site remediation goal in 20 of 36 PDB groundwater samples collected during the August 2014 event.
The site TCE plume is well defined, within the groundwater use restriction boundary in each aquifer zone, to concentrations below the 5-µg/L remediation goal (Figures 3-15 through 3-20).
As discussed in Section 3.2.1, there is an upgradient offsite TCE plume located west of the site present in the I2 and D1 aquifer zones. No specific sources have been identified, and it has been determined that this plume is not related to the Fruit Avenue site presumed source. EPA and NMED will continue to monitor this plume.
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4.3 Contaminant Concentration Trends in Groundwater Based on the evaluation of TCE concentration trends for the period from February 2002 through August 2014 (Figures 3‐21 through 3‐25), TCE concentrations have decreased at most monitor well locations. TCE concentrations continue to fluctuate (D3) or increase at MNW‐5 (D1 and D2) and MNW‐14 (I2), and previously elevated TCE concentrations at the McDonalds (D2) well observed in 2011, 2012, and 2013 are now decreasing. Specific portions of the TCE plume that have experienced changes include the following:
Capture Zone: Within the capture zone of the P&T system in the D2 aquifer zone, there is a continued increase in the TCE concentration at SFMW‐23 (D2).
Downgradient of the P&T system: TCE concentration fluctuations are evident in the D1 and D2 aquifer zones at MNW‐5, while decreases in TCE concentration are observed in the D3 aquifer zone. TCE concentrations are increasing at MNW‐4 (D2) but remain below the remedial goals.
Presumed Source Area: At HSM‐I2‐5, TCE concentrations have decreased from a maximum observed concentration of 99 µg/L in April 2005 and have been fairly stable, between 20 and 32 µg/L, since 2009. (Figure 3‐22).
Western Boundary of the Plume: Southwest of the presumed source area, encroachment of the offsite/upgradient TCE plume onto the FAP site is likely the cause of TCE concentration increases observed at several monitor wells (such as SFMW‐27[I2] and MNW‐1 [I2]), and may also be responsible for increasing TCE concentrations at MNW‐14 (I2). EPA and NMED, through the FSP, are continuing to monitor the upgradient offsite plume.
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Recommendations Based on information presented in the Final Monitored Natural Attenuation Report (CH2M HILL, 2013a), EPA is considering modifying the groundwater remedy to expand monitored natural attenuation (MNA) to include the central and western portions of the FAP site TCE plume. Concurrent with this potential modification, the P&T system has been placed in standby mode after meeting the criteria established in the remedial system evaluation (CH2M HILL, 2009b), while monthly performance sampling, and LTM program groundwater monitoring and reporting continue per the current schedule. While in standby mode, samples of the ASTP influent will continue to be collected during quarterly performance monitoring events to demonstrate the operability of the ASTP. The collection of effluent samples is considered to be unnecessary because of the long history of documented system effectiveness, and therefore it is recommended that these samples be excluded from future sampling events. Continued monitoring of the system’s functionality (blower operation and tray status) can be performed as part of quarterly inspections.
The current groundwater monitoring network and sampling schedule generally is sufficient to develop the information needed to confirm that the remedy modification under consideration is protective of human health and the environment. Some additional MNA‐specific sampling was recommended by the Final Monitored Natural Attenuation Report (CH2M HILL, 2013a), and several changes to monitor well sampling frequency have been made since the last FSP revision. Therefore, an addendum to the FSP will be issued to direct subsequent LTM sampling events and the next MNA sampling event, which is expected to be conducted in February 2015.
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Works Cited CH2M HILL. 2009a. Long‐Term Monitoring Optimization Version 1.2, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. September 29.
CH2M HILL. 2009b. Remedial System Evaluation Version 1.2, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. September.
CH2M HILL. 2010a. Field Sampling Plan, Version 2.1, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. March.
CH2M HILL. 2010b. Quality Assurance Project Plan, Version 4.0, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. March.
CH2M HILL. 2010c. Fruit Avenue Plume Superfund Site, Sampling and Analysis Plan, Version 2.1 – Addendum No. 1. December 3.
CH2M HILL. 2010d. Fruit Avenue Plume Superfund Site ‐ Monitor Well Abandonment Rationale. October 15.
CH2M HILL. 2012. Annual Groundwater Sampling Report for 2011, Fruit Avenue Plume Superfund Site. January 27.
CH2M HILL. 2013a. Monitored Natural Attenuation Evaluation Report.
CH2M HILL. 2013b. Cleanup Status Report No. 40 – Final, Period of March 29, 2013 to June 28, 2013, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. June.
CH2M HILL. 2013c. Annual Groundwater Sampling Report for 2012, Fruit Avenue Plume Superfund Site. January 18.
CH2M HILL. 2014a. Summary of the First Semiannual Groundwater Sampling Event for 2014, Fruit Avenue Plume Superfund Site. June 27.
CH2M HILL. 2014b. Annual Groundwater Sampling Report for 2013, Fruit Avenue Plume Superfund Site. January 17.
U.S. Environmental Protection Agency (EPA). 2001. Record of Decision, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. CERCLIS ID# NMD986668911. September.
U.S. Environmental Protection Agency (EPA). 2006. Explanation of Significant Differences, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. CERCLIS ID# NMD986668911. September.
U.S. Geological Survey (USGS). 2003. Simulated Effects of Ground‐Water Management Scenarios on the Santa Fe Group Aquifer System, Middle Rio Grande Basin, New Mexico, 2001‐40. U.S. Geological Survey Water‐Resources Investigations Report 03‐4040.
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Tables
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TABLES
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TABLE 2‐1Monitor Well and PDB Installation DetailsFruit Avenue Plume Superfund Site, Albuquerque, New Mexico
HSM‐I2‐5 (I2) 117 87 ‐ 107 20 I2 17McDonalds (D2) 251 236 ‐ 251 15 D2 8MNW‐1 (I2) 115 85 ‐ 108 20 I2 7MNW‐4 (D2) 432 402 ‐ 422 20 D2 7MNW‐5 (D1) 246 216 ‐ 236 20 D1 7, 12MNW‐5 (D2) 302 272 ‐ 292 20 D2 7MNW‐5 (D3) 390 360 ‐ 380 20 D3 17MNW‐8 (I2) 115 90 ‐ 110 20 I2 7MNW‐9 (I2) 115 90 – 110 20 I2 17MNW‐9 (D1) 161 130 ‐ 150 20 D1 2MNW‐11 (D1) 140 110 ‐ 130 20 D1 2MNW‐14 (I2) 110.4 95.4 ‐ 105.4 10 I2 2, 8MNW‐14 (D1) 194.9 164.9 ‐ 184.9 20 D1 7SFMW‐14 (D1) 166.3 156 ‐ 166 10 D1 2SFMW‐17 (I2) 102.9 92.7 ‐ 102.7 10 I2 8SFMW‐18 (I1) 85 74.8 ‐ 84.8 10 I1 8SFMW‐20 (I1) 85 74.8 – 84.8 10 I1 5SFMW‐21 (I2) 103.7 83.4 – 103.5 20 I2 12, 17SFMW‐22 (D1) 192.4 181.9 ‐ 191.9 10 D1 8SFMW‐23 (D2) 240.2 229.7 – 239.7 10 D2 5SFMW‐25 (I1) 85.2 74.9 – 84.9 10 I1 5SFMW‐26 (I2) 105 94.8 – 104.8 10 I2 2, 8SFMW‐27 (I2) 103.9 93.7 ‐ 103.7 10 I2 8SFMW‐35 (D3) 320.7 310.3 ‐ 320.3 10 D3 5SFMW‐44 (D2) 268.3 248 – 268 20 D2 12, 17SFMW‐47 (I1/I2) 110.7 80.2 – 110.2 30 I1/I2 12, 22aSee sampling and analysis plan for discussion of site hydrogeology and aquifer zone designations. Aquifer Zone Designations:I1 = Intermediate Zone 1, I2 = Intermediate Zone 2, D1 = Deep Zone 1, D2 = Deep Zone 2, D3 = Deep Zone 3, D4 = Deep Zone 4Notes:bgs = below ground surfacePDB = passive diffusion bag
Aquifer Zone Designationa
Depths of Sampled PDBs(feet below top of screen)
Monitor Well ID Total Well Depth (feet bgs) Screened Interval (feet bgs) Length of Well Screen (feet)
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TABLE 2‐2Planned Sampling Frequency for Site WellsFruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monthlya Semiannuala
(February and August)Annuala
(February Every Year)
Bienniala
(February During Odd‐Numbered Years)
DM‐05(S)DM‐09(S)
SFMW‐20(I1) DM‐12(I1) MNW‐8(I1)SFMW‐25(I1) DM‐06(I1/I2) MNW‐9(I1)
SFMW‐47(I1/I2) DM‐07(I1/I2) MNW‐11(I1)SFMW‐18(I1) DM‐08(I1/I2) MNW‐12(I1)
SFMW‐16(I1) SFMW‐12(I1)WB‐01(I1/I2)WB‐02(I1/I2)
HSM‐I2‐5(I2) DM‐06(I1/I2) MNW‐2(I2)SFMW‐26(I2) DM‐07(I1/I2) MNW‐11(I2)
SFMW‐47(I1/I2) DM‐08(I1/I2) MNW‐12(I2)MNW‐1(I2) SFMW‐37(I2) SFMW‐13(I2)MNW‐8(I2) SFMW‐10(I2) SFMW‐28(I2)b
MNW‐9(I2) SFWM‐31(I2)MNW‐14(I2) SFMW‐32(I2)SFMW‐17(I2) MNW‐10(I2)SFMW‐21(I2) WB‐01(I1/I2)SFMW‐27(I2) WB‐02(I1/I2)MNW‐9(D1) MNW‐4(D1) MNW‐3(D1)
MNW‐11(D1) MNW‐13(D1) MNW‐6(D1)MNW‐5(D1) MNW‐16(D1) MNW‐15(D1)
SFMW‐22(D1) MNW‐12(D1)SFMW‐14 (D1) SFMW‐38(D1)MNW‐14(D1) SFMW‐46(D1/D2)
D2E‐P1 MNW‐4(D2) MNW‐13(D2) MNW‐3(D2)MNW‐5(D2) MNW‐16(D2) MNW‐6(D2)
SFMW‐23(D2) SFMW‐39(D2) MNW‐9(D2)SFMW‐44(D2) SFMW‐46(D1/D2) MNW‐11(D2)
McDonalds(D2)b MNW‐12(D2)MNW‐15(D2)SFMW‐33(D2)SFMW‐45(D2)
Deep‐3 (D3) MNW‐5(D3) MNW‐4(D3) MNW‐3(D3)SFMW‐35(D3) MNW‐6(D3) MNW‐15(D3)
SFMW‐41(D3/D4) MNW‐13(D3)MNW‐16(D3)SFMW‐40(D3)
SFMW‐41(D3/D4) MNW‐5(D4) MNW‐7(D4)
MNW‐16(D4)
Number of Wells per Event 1 27 24 30Total Notes:aEach sampling event would include the wells sampled with greater frequency (i.e., wells sampled semiannually would be sampled during the annual and biannual sampling events).
bDenotes monitor wells where sampling is being performed semiannually to select the appropriate PDB interval for sampling.
Deep‐2 (D2)
Deep‐1 (D1)
82
Deep‐4 (D4)
Aquifer Zone
Proposed Monitor Wells to be Sampled by Sampling Frequency
Shallow
Intermediate‐1 (I1)
Intermediate‐2 (I2)
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TABLE 2‐3Water Level Measurements, August 24, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monitor Well IDAquifer ZoneDesignationa
TOC Elevation (feet amsl)
Depth to Water(Feet BTOC)
Water Level Elevation
(feet amsl)Date
DM‐01 S 4954.80 32.40 4922.40 24‐Aug‐14DM‐05 S 4954.92 33.15 4921.77 24‐Aug‐14DM‐06 I1/I2 4953.60 36.72 4916.88 24‐Aug‐14DM‐07 I1/I2 4954.35 36.82 4917.53 24‐Aug‐14DM‐08 I1/I2 4954.85 36.81 4918.04 24‐Aug‐14DM‐09 S 4954.83 35.05 4919.78 24‐Aug‐14DM‐10 S 4954.24 36.20 4918.04 24‐Aug‐14DM‐11 S 4954.15 28.88 4925.27 24‐Aug‐14DM‐12 I1/I2 4953.79 27.57 4926.22 24‐Aug‐14DM‐13 (S) S 4954.11 32.59 4921.52 24‐Aug‐14DM‐13 (I1)b I1 4954.11 31.84 4922.27 24‐Aug‐14DM‐13 (I2)b D1 4954.09 30.92 4923.17 24‐Aug‐14DM‐13 (D1)b D2 4954.08 28.24 4925.84 24‐Aug‐14HSM‐I2‐4 I2 4957.10 31.10 4926.00 24‐Aug‐14HSM‐I2‐5 I2 4957.10 32.60 4924.50 24‐Aug‐14McDonald's D2 4959.00 44.79 4914.21 24‐Aug‐14MNW‐1 (I2) I2 4955.20 25.24 4929.96 24‐Aug‐14MNW‐2 (I2) I2 4956.10 30.42 4925.68 24‐Aug‐14MNW‐3 (D1) D1 4972.50 57.72 4914.78 24‐Aug‐14MNW‐3 (D2) D2 4972.50 58.90 4913.60 24‐Aug‐14MNW‐3 (D3) D3 4972.50 59.86 4912.64 24‐Aug‐14MNW‐4 (D1) D1 5061.40 155.78 4905.62 24‐Aug‐14MNW‐4 (D2) D2 5061.40 155.52 4905.88 24‐Aug‐14MNW‐4 (D3) D3 5061.40 155.09 4906.31 24‐Aug‐14MNW‐5 (D1) D1 4993.60 83.79 4909.81 24‐Aug‐14MNW‐5 (D2) D2 4993.60 83.49 4910.11 24‐Aug‐14MNW‐5 (D3) D3 4993.60 83.30 4910.30 24‐Aug‐14MNW‐5 (D4) D4 4992.51 82.13 4910.38 24‐Aug‐14MNW‐6 (D1) D1 4967.90 56.02 4911.88 24‐Aug‐14MNW‐6 (D2) D2 4967.90 55.91 4911.99 24‐Aug‐14MNW‐6 (D3) D3 4967.90 55.82 4912.08 24‐Aug‐14MNW‐7 (D4) D4 5012.30 102.32 4909.98 24‐Aug‐14MNW‐8 (I1) I1 4954.60 24.23 4930.37 24‐Aug‐14MNW‐8 (I2) I2 4954.70 24.13 4930.57 24‐Aug‐14MNW‐9 (I1) I1 4954.60 20.92 4933.68 24‐Aug‐14MNW‐9 (I2) I2 4954.60 22.72 4931.88 24‐Aug‐14MNW‐9 (D1) D1 4954.37 22.62 4931.75 24‐Aug‐14MNW‐9 (D2) D2 4954.36 22.45 4931.91 24‐Aug‐14MNW‐11 (D1) D1 4954.47 20.74 4933.73 24‐Aug‐14MNW‐12 (I1) I1 4954.34 20.52 4933.82 24‐Aug‐14MNW‐12 (I2) I2 4954.37 20.57 4933.80 24‐Aug‐14MNW‐12 (D1) D1 4954.32 20.49 4933.83 24‐Aug‐14
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011352
TABLE 2‐3Water Level Measurements, August 24, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monitor Well IDAquifer ZoneDesignationa
TOC Elevation (feet amsl)
Depth to Water(Feet BTOC)
Water Level Elevation
(feet amsl)Date
MNW‐12 (D2) D2 4954.36 20.57 4933.79 24‐Aug‐14MNW‐13 (D1) D1 5071.72 165.30 4906.42 24‐Aug‐14MNW‐13 (D2) D2 5071.76 165.11 4906.65 24‐Aug‐14MNW‐13 (D3) D3 5071.64 164.49 4907.15 24‐Aug‐14MNW‐13 (D4) D4 5071.71 164.05 4907.66 24‐Aug‐14MNW‐14 (I2) I2 4955.64 28.51 4927.13 24‐Aug‐14MNW‐14 (D1) D1 4955.64 26.88 4928.76 24‐Aug‐14MNW‐14 (D2) D2 4955.63 26.52 4929.11 24‐Aug‐14MNW‐15 (D1) D1 5123.53 230.48 4893.05 24‐Aug‐14MNW‐15 (D2) D2 5123.52 220.55 4902.97 24‐Aug‐14MNW‐15 (D3) D3 5123.45 220.30 4903.15 24‐Aug‐14MNW‐16 (D1) D1 5065.93 159.46 4906.47 24‐Aug‐14MNW‐16 (D2) D2 5065.95 158.93 4907.02 24‐Aug‐14MNW‐16 (D3) D3 5065.92 158.67 4907.25 24‐Aug‐14MNW‐16 (D4) D4 5066.00 158.38 4907.62 24‐Aug‐14SFMW‐01 S 4954.29 31.05 4923.24 24‐Aug‐14SFMW‐03 S 4953.99 32.27 4921.72 24‐Aug‐14SFMW‐07 S 4953.48 29.70 4923.78 24‐Aug‐14SFMW‐10 I2 4953.85 28.01 4925.84 24‐Aug‐14SFMW‐11 S 4954.83 27.72 4927.11 24‐Aug‐14SFMW‐12 I1 4954.69 27.53 4927.16 24‐Aug‐14SFMW‐13 I2 4954.59 27.41 4927.18 24‐Aug‐14SFMW‐14 D1 4953.77 26.38 4927.39 24‐Aug‐14SFMW‐15 S 4954.31 33.97 4920.34 24‐Aug‐14SFMW‐16 I1 4954.53 33.46 4921.07 24‐Aug‐14SFMW‐17 I2 4954.55 32.12 4922.43 24‐Aug‐14SFMW‐18 I1 4952.96 28.80 4924.16 24‐Aug‐14SFMW‐20 I1 4954.96 42.90 4912.06 24‐Aug‐14SFMW‐21 I2 4954.76 42.53 4912.23 24‐Aug‐14SFMW‐22 D1 4954.80 42.22 4912.58 24‐Aug‐14SFMW‐23 D2 4954.86 42.60 4912.26 24‐Aug‐14SFMW‐24 S 4952.65 32.85 4919.80 24‐Aug‐14SFMW‐25 I1/I2 4952.75 33.97 4918.78 24‐Aug‐14SFMW‐26 I2 4952.69 34.30 4918.39 24‐Aug‐14SFMW‐27 I2 4953.70 27.26 4926.44 24‐Aug‐14SFMW‐28 I2 4952.24 NA ‐ 24‐Aug‐14SFMW‐31 I2 4955.46 50.64 4904.82 24‐Aug‐14SFMW‐32 I2 4963.63 57.79 4905.84 24‐Aug‐14SFMW‐33 D2 4954.06 39.00 4915.06 24‐Aug‐14SFMW‐34 D4 4954.04 43.05 4910.99 24‐Aug‐14SFMW‐35 D3 4954.64 43.55 4911.09 24‐Aug‐14SFMW‐36 D4 4954.64 44.53 4910.11 24‐Aug‐14SFMW‐37 I2 4953.36 38.61 4914.75 24‐Aug‐14SFMW‐38 D1 4963.92 55.64 4908.28 24‐Aug‐14SFMW‐39 D2 4962.40 54.21 4908.19 24‐Aug‐14
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 2‐3 ES110514201639SPB PAGE 2 OF 3
011353
TABLE 2‐3Water Level Measurements, August 24, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monitor Well IDAquifer ZoneDesignationa
TOC Elevation (feet amsl)
Depth to Water(Feet BTOC)
Water Level Elevation
(feet amsl)Date
SFMW‐40 D3 4963.18 55.59 4907.59 24‐Aug‐14SFMW‐41 D3/D4 4963.14 56.11 4907.03 24‐Aug‐14SFMW‐43 I1 4967.52 63.00 4904.52 24‐Aug‐14SFMW‐44 D2 4967.57 58.06 4909.51 24‐Aug‐14SFMW‐45 D2 5001.06 92.28 4908.78 24‐Aug‐14SFMW‐46 D1/D2 5026.05 120.07 4905.98 24‐Aug‐14SFMW‐47 I1/I2 4954.11 32.04 4922.07 24‐Aug‐14SPSC‐MW5 S 4956.61 38.55 4918.06 24‐Aug‐14SPSC‐MW19 S 4954.77 41.22 4913.55 24‐Aug‐14SPSC‐W13c S 4952.02 39.35 4912.67 24‐Aug‐14WB‐01 (I) I1/I2 4954.05 26.19 4927.86 24‐Aug‐14WB‐02 (I) I1/I2 4954.05 25.09 4928.96 24‐Aug‐14
0 104 103 103 104
Notes:
bDM‐13 (I1), (I2), and (D1) are former I, D1; and D2, respectively. They were renamed in 2005. c Well was paved over Notes:BTOC = below top of casingamsl = above mean sea levelNA = Not Accessable due to construction activititesAquifer Zone Designations:S = Shallow ZoneI1 = Intermediate Zone 1I2 = Intermediate Zone 2D1 = Deep Zone 1D2 = Deep Zone 2D3 = Deep Zone 3D4 = Deep Zone 4
aSee sampling and analysis plan for discussion of site hydrogeology and aquifer zone designations.
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 2‐3 ES110514201639SPB PAGE 3 OF 3
011354
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011355
TABLE 3‐1Horizontal Groundwater Flow Gradients between Selected Monitor Wells for Each Aquifer ZoneFruit Avenue Plume Superfund Site, Albuquerque, New Mexico
August 2006 February 2007 September 2007 April 2008 October 2008 April 2009 October 2009 January 2010 August 2010 February 2011 August 2011 February 2012 August 2012 February 2013 August 2013 February 2014 August 2014 Comment
WB‐01 (S)SFMW‐07SFMW‐07SFMW‐24SFMW‐24SPSC‐W19
MNW‐11 (I1)WB‐01 (I)WB‐01 (I)SFMW‐18SFMW‐18
DM‐06 Near the railroad trackDM‐06
SFMW‐20SFMW‐20SFMW‐43
MNW‐11 (I2)WB‐01 (I)WB‐01 (I)SFMW‐27WB‐01 (I)
MNW‐14 (I2)SFMW‐27
DM‐06MNW‐14 (I2)
DM‐06 Near the railroad trackDM‐06
SFMW‐21SFMW‐21SFMW‐31
MNW‐11 (D1)MNW‐14 (D1)
SFMW‐14DM‐13 (D1)
MNW‐14 (D1)SFMW‐22
DM‐13 (D1)SFMW‐22SFMW‐38SFMW‐46SFMW‐22
MNW‐5 (D1)MNW‐5 (D1)MNW‐4 (D1)MNW‐4 (D1)
MNW‐15 (D1)MNW‐16 (D1)MNW‐15 (D1)
MNW‐5 (D1)MNW‐15 (D1)
0.0013 0.0017
0.0019 0.0024
0.0109 0.0095
0.0118 0.0107
0.0071 0.0067
0.0024 0.0023
0.0013 0.0013
0.0095 0.0095
0.0107 0.0108
0.0010 0.0014
0.0009 0.0007
0.0088 0.0087
0.0118 0.0119
0.0058 0.0053
0.0170 0.0158
0.0085 0.0086
0.0060 0.0056
0.0089 0.0082
0.0051 0.0050
0.0018 0.0018
#N/A #N/A
0.0065 0.0064
0.0047 0.0064
0.0042 0.0041
0.0052 0.0051
0.0132 0.0109
0.0077 0.0069
0.0114 0.0125
0.0009 0.0020
0.0014 0.0021
0.0020 0.0027
0.0121 0.0096
0.0060
0.0191 0.0171
0.0025 0.0025
0.0014 0.0014
0.0099 0.0108
0.0087 0.0087
0.0071 0.0071
0.0101 0.0101
0.0053 0.0052
0.0019 0.0019
‐‐ ‐‐
0.0067 0.0070
0.0071 0.0074
0.0043 0.0043
0.0055 0.0055
Horizontal Groundwater Flow Gradients (ft/ft)a
Shallow Aquifer Zone
Intermediate 1 Aquifer Zone
Intermediate 2 Aquifer Zone
Deep 1 Aquifer Zone
Across the extraction well
Across the extraction well
N/A N/A
0.0014
0.0014
0.0111
0.0129
0.0024
N/A N/A N/A N/A N/A N/A N/A N/A N/A
0.0018 0.0036
0.0027 0.0038
0.0110 0.0085
0.0139
0.0150
N/A
0.0030
Across the extraction well
Across the extraction well
0.0014 0.0015
0.0085 0.0098
0.0126 0.0131
0.0068 0.0066
‐0.0015 0.0184
0.0024 0.0025
0.0039
0.0107
0.0096
0.0011 0.0010
0.0090 0.0095
0.0121 0.0127
0.0066
0.0093 0.0098
0.0072 0.0069
0.0103 0.0100
0.0044 0.0044
0.0046 0.0029
‐‐ ‐‐
‐0.0052 0.0072
0.0078 ‐0.0024
0.0044 0.0043
0.0055 0.0055
0.0076 0.0071
0.0026 0.0027
0.0015 0.0015
0.0116 0.0118
0.0137 0.0139
0.0016 0.0029
0.0099 0.0103
0.0131 0.0135
0.0071 0.0082
0.0202 0.0164
‐‐ ‐‐
0.0076 0.0073
0.0108 0.0102
0.0055 0.0054
0.0020 0.0021
0.0011 0.0014
0.0072 0.0075
0.0082 0.0084
0.0045 0.0044
0.0057 0.0057
0.0097 0.0103
0.0203
0.0120
0.0083
0.0124
0.0120
0.0128
0.0029
0.0022
0.0078 0.0084
0.0119
0.0121
0.0026
0.0034 0.0030
0.0033
0.0025
0.0104
0.0151
0.0030
0.01270.0139
0.0011
0.00740.0074
0.0093
0.00390.0037
0.0125
N/A
N/A
N/A
0.0191
0.0029
0.0028
N/A
0.0142
0.00430.0035
0.0034 0.0034
0.0091
N/A
0.0129
0.0089
0.0025
N/A
0.0036
0.0033
0.0070
0.0060
0.0132
0.0100
0.0091
0.0066
0.0036
0.0059
0.0103
0.0124
0.0060
0.0134
0.0038
0.0058
0.0059
0.0029
0.0041
0.0187 0.0193
0.0080
0.0023
0.0029
0.0121
0.0087 0.0086
0.0111
0.0116
0.0087
N/A
0.0158
0.0130 0.0122
0.0016
0.0084
0.0153
0.0117
0.0014
0.0192
0.0086 0.0083
0.0017
0.008
0.0004
0.0030
0.0087
N/A
0.0107
N/A
0.0057
0.0119
0.0084
0.0098
0.0023 0.0024 0.00160.0022
0.0168
N/A 0.0044
0.0178
0.0031
0.0195
0.0058
0.0117
0.00580.0063
0.0021
0.0046
0.0110
0.0130
0.0082
0.0017
0.0014 0.0018
0.003
0.0024
0.0150 0.0155
0.0202
0.0115
0.00960.0089 0.009
0.00560.00610.0064 0.0065 0.0061 0.00660.0066
0.0047
0.0083
0.0074
0.0099 0.01030.0106
Aquifer Zone Monitor Well ID
0.0099
0.0049
0.0098
0.00510.00480.0050
0.0065
0.0082 0.0108
0.0065 0.00710.0067
0.0103
0.00700.0068 0.0065 0.0061
0.00770.0081
0.0096 0.0086
0.0046 0.0046
0.0085
0.0047
0.0084
0.0047
0.0061 0.0058
0.0109 0.0106
0.0088 0.0073
0.0114 0.0111
0.0056 0.0056
0.0021 0.0020
0.0014 0.0012
0.0110 0.0106
0.0143 0.0140
0.0083 0.0070
0.0212 0.0203
0.0028 0.0027
0.0044 0.0016
0.0115 0.0118
0.0107 0.0138
0.0014 0.0024
0.0018 0.0031
0.0026 0.0026
0.0129 0.0111
0.0086 0.0076
0.0019 0.0027
0.0025 0.0035
0.0114 0.0099
0.0077 0.0076
N/A 0.0142
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3-1 ES110514201639SPB PAGE 1 OF 2
011356
TABLE 3‐1Horizontal Groundwater Flow Gradients between Selected Monitor Wells for Each Aquifer ZoneFruit Avenue Plume Superfund Site, Albuquerque, New Mexico
August 2006 February 2007 September 2007 April 2008 October 2008 April 2009 October 2009 January 2010 August 2010 February 2011 August 2011 February 2012 August 2012 February 2013 August 2013 February 2014 August 2014 Comment
Horizontal Groundwater Flow Gradients (ft/ft)a
Aquifer Zone Monitor Well ID
MNW‐11 (D2)MNW‐14 (D2)MNW‐14 (D2)
SFMW‐33 Near the railroad trackSFMW‐33SFMW‐23SFMW‐39SFMW‐46SFMW‐23
MNW‐5 (D2)MNW‐5 (D2)MNW‐4 (D2)MNW‐4 (D2)
MNW‐15 (D2)MNW‐16 (D2)MNW‐15 (D2)MNW‐5 (D2)
MNW‐15 (D2)SFMW‐35
MNW‐5 (D3)SFMW‐40
MNW‐4 (D3)MNW‐5 (D3)MNW‐4 (D3)MNW‐4 (D3)
MNW‐15 (D3)MNW‐16 (D3)MNW‐15 (D3)MNW‐5 (D3)
MNW‐15 (D3)SFMW‐34
MNW‐5 (D4)MNW‐5 (D4)
MNW‐13 (D4)MNW‐5 (D4)
MNW‐16 (D4)SFMW‐34
MNW‐7 (D4)aHorizontal groundwater flow gradient calculated from west to east in the direction of groundwater flow at each well pair. A negative gradient indicates a reverse flow direction.
Notes:ft/ft = foot per footN/A = Not applicable because one or both wells used to calculate horizontal flow gradient had not yet been installed or were inaccessible.‐‐‐ = Gradient not calculated as well WB‐01 (S) was plugged and abandoned in early 2011.
0.0002 0.0003
0.0016 0.0018
0.0020 0.0022
0.0002 0.0003
0.0003 0.0007
0.0022 0.0023
0.0021 0.0024
0.0029 0.0033
0.0026 0.0028
0.0021 0.0024
0.0020 0.0022
0.0029 0.0032
0.0025 0.0028
0.0001 0.0005
0.0022 0.0022
0.0135 0.0136
0.0038 0.0041
0.0010 0.0014
0.0010 0.0014
0.0002 0.0004
0.0029 0.0037
0.0025 0.0033
0.0002 0.0014
0.0018 0.0015
0.0021 0.0009
0.0025 0.0034
0.0004 0.0009
0.0004 0.0011
0.0019 0.0026
0.0022 0.0029
0.0007 0.0018
0.0010 0.0016
0.0020 0.0027
0.0021 0.0028
0.0029 0.0037
0.0023 0.0023
0.0139 0.0148
0.0046 0.0057
Deep 2 Aquifer Zone
Deep 3 Aquifer Zone
Deep 4 Aquifer Zone
N/A N/A N/A N/A N/A N/A N/A N/A N/AN/A N/A N/A
N/A N/A N/A N/A N/A N/A N/A 0.0023
N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 0.0052N/A
N/A
0.0015
0.0044
0.0026 0.0033
0.0031 0.0041
0.0005 0.0009
0.0023 0.0033
0.0004 0.0008
0.0024 0.0030
0.0031 0.0041
0.0015 0.0022
0.0011 0.0021
0.0025 0.0034
0.0148 0.0158
0.0062 0.0071
0.0010 0.0021
0.0019 0.0030
0.0027 0.0037
0.0024 0.0025
0.0008 0.0005
0.0008 0.0005
0.0025 0.0023
0.0169
0.0028 0.0029
0.0034
0.0027
0.0038 0.0036
0.0030 0.0031
0.0056
0.0018 0.0022
0.0022
0.0072
0.0032 0.0028
0.0036
0.0018 0.0014
0.0027 0.0028
0.0030
0.0172
0.0022 0.0012
0.0038
0.0188
0.0044
0.0027
0.0026
0.0039
0.0028
0.0036
0.0065
0.0027
0.0174
0.0032
0.0011
0.0028
0.0027
0.00340.0038
0.0016
0.0035
0.0019
0.0020
N/A N/A
0.004
0.0035
0.0013
0.0025 0.0034
0.0009
0.0037
0.00230.0022
0.00350.0031
N/A N/A
0.0025
0.0033
0.0022
0.0024
0.0019
0.0030
0.0026 0.0029
0.0009
0.0025
0.0013 0.0012
0.0007
0.0017
0.0016
0.0025
0.0041
0.0028
0.0043
0.0014
0.00240.0020
0.0011
0.0035
0.0034
0.0021
0.0042
0.0038
0.004
0.0075
0.0038
0.0012
0.0042
0.0019
0.0038
0.0034
0.0024
0.0085
0.0036
0.0057
0.0028
0.0069
0.0164 0.01900.0180
0.00290.0042 0.0026 0.0026
0.0161 0.0157
0.0048 0.0068
0.0014 0.0017
0.0015 0.0026
0.0026 0.0032
0.0023 0.0029
0.0030 0.0037
0.0008 0.0020
0.0010 0.0013
0.0004 0.0006
0.0025 0.0030
0.0025 0.0031
0.0030 0.0037
0.0008 0.0007
0.0015 0.0025
0.0025 0.0024
0.0021 0.0026
0.0033 0.0036
0.0005 0.0017
0.0006 0.0013
N/A 0.0148
N/A 0.0063
0.0009 0.0016
0.0008 0.0023
0.0031 0.0033
0.0051
N/A 0.0006
0.0024 0.0031
0.0021 0.0028
0.0027 0.0036
N/A 0.0006
0.0020 0.0023
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3-1 ES110514201639SPB PAGE 2 OF 2
011357
TABLE 3‐2Vertical Groundwater Flow Direction at Selected Monitor Well Locations Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Vertical Groundwater Flow
Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Groundwater Flow
Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Groundwater Flow
Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Groundwater Flow
Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Groundwater Flow
Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
SFMW‐07 SSFMW‐18 I1/I2
MNW‐14 (I2) I2MNW‐14 (D1) D1MNW‐14 (D2) D2
DM‐13 (S) SDM‐13 (I) I1
DM‐13 (I2) I2DM‐13 (D1) D1SFMW‐15 SSFMW‐16 I1/I2SFMW‐17 I2SFMW‐24 SSFMW‐25 I1/I2SFMW‐26 I2SFMW‐33 D2SFMW‐34 D4SFMW‐20 I1/I2SFMW‐21 I2SFMW‐22 D1SFMW‐23 D2SFMW‐35 D3SFMW‐36 D4SFMW‐32b I2SFMW‐38 D1SFMW‐39 D2
MNW‐3 (D1) D1MNW‐3 (D2) D2MNW‐3 (D3) D3MNW‐5 (D1) D1MNW‐5 (D2) D2MNW‐5 (D3) D3MNW‐5 (D4) D4
MNW‐15 (D1) D1MNW‐15 (D2) D2MNW‐15 (D3) D3MNW‐16 (D1) D1MNW‐16 (D2) D2MNW‐16 (D3) D3MNW‐16 (D4) D4
bSee Section 3.1.2 in text.Notes:
ft/ft = foot per foot
up ‐9.42 ‐4.71
up ‐0.21 up ‐0.58 up ‐0.62 up ‐0.64
Eastern Site Boundary
up ‐1.24
N/A N/A N/A N/A N/A N/A N/A N/A N/A
October 2007
up
‐3.36
down 2.33
Divergent from D1
up
‐6.07
9.03down
N/A
Divergent from D2
‐3.21
2.07
down
up‐7.69
down
up
7.87
Divergent from D1 Divergent from D1
down 6.35
down down
3.84
‐1.04Divergent from D1
down
2.30
4.12
Divergent from D1 ‐2.46
2.40
3.55
N/AN/A
February 2007
‐6.16
Presumed Source Area
‐3.46upup up‐6.07
up
up ‐3.12 up
up ‐2.12
Area of the Plume
Monitor Well ID
July 2005
‐5.84
‐5.43
August 2006
Aquifer Zone
up
February 2006
down 7.52
Divergent from D1
up ‐3.43
11.17
SFMW‐40
down
‐3.22up
2.08
Divergent from D1
down
‐4.43
3.80Divergent from D1
down 7.18
3.40down
Central Plume Area
D3
down 4.88
9.37
2.67down
down 4.81
2.62
5.89
aDifference in water level elevation is between all wells at the particular location where vertical gradients were calculated.
N/A = Vertical gradient not calculated because the wells had not yet been installed or were inaccessible.
Negative values indicate an upward flow gradient. Positive values indicate a downward flow gradient.
N/A ‐9.66 up
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐2ES110514201639SPB PAGE 1 OF 4
011358
TABLE 3‐2Vertical Groundwater Flow Direction at Selected Monitor Well Locations Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
SFMW‐07 SSFMW‐18 I1/I2
MNW‐14 (I2) I2MNW‐14 (D1) D1MNW‐14 (D2) D2
DM‐13 (S) SDM‐13 (I) I1
DM‐13 (I2) I2DM‐13 (D1) D1SFMW‐15 SSFMW‐16 I1/I2SFMW‐17 I2SFMW‐24 SSFMW‐25 I1/I2SFMW‐26 I2SFMW‐33 D2SFMW‐34 D4SFMW‐20 I1/I2SFMW‐21 I2SFMW‐22 D1SFMW‐23 D2SFMW‐35 D3SFMW‐36 D4SFMW‐32b I2SFMW‐38 D1SFMW‐39 D2
MNW‐3 (D1) D1MNW‐3 (D2) D2MNW‐3 (D3) D3MNW‐5 (D1) D1MNW‐5 (D2) D2MNW‐5 (D3) D3MNW‐5 (D4) D4
MNW‐15 (D1) D1MNW‐15 (D2) D2MNW‐15 (D3) D3MNW‐16 (D1) D1MNW‐16 (D2) D2MNW‐16 (D3) D3MNW‐16 (D4) D4
bSee Section 3.1.2 in text.Notes:
ft/ft = foot per foot
aDifference in water level elevation is between all wells at the particular location where vertical gradients were calculated.
N/A = Vertical gradient not calculated because the wells had not yet been installed or were inaccessible.
Negative values indicate an upward flow gradient. Positive values indicate a downward flow gradient.
Area of the Plume
Monitor Well ID Aquifer Zone
Presumed Source Area
Central Plume Area
SFMW‐40 D3
Eastern Site Boundary
up ‐12.74up
N/A N/A N/A N/A N/A N/A N/A
‐0.68‐0.63 up ‐1.16 up ‐0.95 up
up ‐14.63
N/A
7.47
up‐8.29
2.39
down
‐10.74
down 3.08
Divergent from D1
‐4.03
6.61
‐2.17
down
April 2009
‐6.09‐5.99‐3.98
down
5.35
NA‐2.03up NA
‐2.09up
October 2008
up
October 2009
up
downup
2.03
‐5.58
up
down1.72 1.96
down
April 2008
up ‐6.6
down
2.08
up
down
6.62
‐3.06
4.53
Divergent from D1
1.30
down 3.89
January 2010
up ‐6.02
up ‐5.39
up ‐1.88
6.78
Divergent from D1
Divergent from D2
0.73
‐6.93
Divergent from D1
down
5.56
Divergent from D1
3.42
Divergent from D1
2.94down
down
Divergent from D1
down
down 1.82 2.60
Divergent from D1
down
2.88
‐5.57
‐9.27
3.86
‐3.96Divergent from D1
up
down
up ‐1.08 up
N/A N/A
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐2ES110514201639SPB PAGE 2 OF 4
011359
TABLE 3‐2Vertical Groundwater Flow Direction at Selected Monitor Well Locations Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest Groundwater
Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest
Groundwater Elevation (feet)a
SFMW‐07 SSFMW‐18 I1/I2
MNW‐14 (I2) I2MNW‐14 (D1) D1MNW‐14 (D2) D2
DM‐13 (S) SDM‐13 (I) I1
DM‐13 (I2) I2DM‐13 (D1) D1SFMW‐15 SSFMW‐16 I1/I2SFMW‐17 I2SFMW‐24 SSFMW‐25 I1/I2SFMW‐26 I2SFMW‐33 D2SFMW‐34 D4SFMW‐20 I1/I2SFMW‐21 I2SFMW‐22 D1SFMW‐23 D2SFMW‐35 D3SFMW‐36 D4SFMW‐32b I2SFMW‐38 D1SFMW‐39 D2
MNW‐3 (D1) D1MNW‐3 (D2) D2MNW‐3 (D3) D3MNW‐5 (D1) D1MNW‐5 (D2) D2MNW‐5 (D3) D3MNW‐5 (D4) D4
MNW‐15 (D1) D1MNW‐15 (D2) D2MNW‐15 (D3) D3MNW‐16 (D1) D1MNW‐16 (D2) D2MNW‐16 (D3) D3MNW‐16 (D4) D4
bSee Section 3.1.2 in text.Notes:
ft/ft = foot per foot
aDifference in water level elevation is between all wells at the particular location where vertical gradients were calculated.
N/A = Vertical gradient not calculated because the wells had not yet been installed or were inaccessible.
Negative values indicate an upward flow gradient. Positive values indicate a downward flow gradient.
Area of the Plume
Monitor Well ID Aquifer Zone
Presumed Source Area
Central Plume Area
SFMW‐40 D3
Eastern Site Boundary
up ‐7.99up ‐11.85‐10.55 up ‐10.31up ‐13.1
down 6.86
Divergent from D1
4.22
Divergent from D1
‐1.79
down 3.64
up
up
up ‐1.68N/A N/A N/A N/A N/A N/A N/A N/A
August 2011
up ‐5.66
up ‐4.86
up ‐2.71
down 1.77
up ‐1.05
Divergent from D1 3.03
Divergent from D1 & Convergent on D2 ‐2.92b
Divergent from D2 2.72
5.76
up ‐1.35 up ‐1.03
NA
1.93
‐4.21
1.77
Divergent from D1
Divergent from D1
down
down
August 2012
up ‐5.69
up ‐4.77
up ‐2.67
down 1.45
up ‐5.62
up ‐4.75
up ‐1.59
down 1.58
February 2012
up ‐1.16
February 2011
up ‐5.72
up ‐4.83
up ‐2.64
down ‐‐
down 5.4
Divergent from D1
2.61
Divergent from D1
‐3.51
down 2.45
down 1.27
down 6.28
August 2010
up ‐5.75
up ‐3.14
up ‐1.76
3.14
Divergent from D1
down 1.74
‐2.9
Divergent from D1
‐1.17
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐2ES110514201639SPB PAGE 3 OF 4
011360
TABLE 3‐2Vertical Groundwater Flow Direction at Selected Monitor Well Locations Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest
Groundwater Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest
Groundwater Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest
Groundwater Elevation (feet)a
Vertical Ground‐water Flow Direction
Difference Between Highest and Lowest
Groundwater Elevation (feet)a
SFMW‐07 SSFMW‐18 I1/I2
MNW‐14 (I2) I2MNW‐14 (D1) D1MNW‐14 (D2) D2
DM‐13 (S) SDM‐13 (I) I1
DM‐13 (I2) I2DM‐13 (D1) D1SFMW‐15 SSFMW‐16 I1/I2SFMW‐17 I2SFMW‐24 SSFMW‐25 I1/I2SFMW‐26 I2SFMW‐33 D2SFMW‐34 D4SFMW‐20 I1/I2SFMW‐21 I2SFMW‐22 D1SFMW‐23 D2SFMW‐35 D3SFMW‐36 D4SFMW‐32b I2SFMW‐38 D1SFMW‐39 D2
MNW‐3 (D1) D1MNW‐3 (D2) D2MNW‐3 (D3) D3MNW‐5 (D1) D1MNW‐5 (D2) D2MNW‐5 (D3) D3MNW‐5 (D4) D4
MNW‐15 (D1) D1MNW‐15 (D2) D2MNW‐15 (D3) D3MNW‐16 (D1) D1MNW‐16 (D2) D2MNW‐16 (D3) D3MNW‐16 (D4) D4
bSee Section 3.1.2 in text.Notes:
ft/ft = foot per foot
aDifference in water level elevation is between all wells at the particular location where vertical gradients were calculated.
N/A = Vertical gradient not calculated because the wells had not yet been installed or were inaccessible.
Negative values indicate an upward flow gradient. Positive values indicate a downward flow gradient.
SFMW‐40 D3
Eastern Site Boundary
Area of the Plume
Presumed Source Area
Central Plume Area
Divergent from D3
0.80 up ‐0.57
up ‐11.98 up ‐10.1
up ‐1.11 up ‐1.15
Divergent from D1
1.81Divergent from
I22.47
Divergent from D1
‐3.68Divergent from
D1‐2.44
down 1.59 down 2.14
up ‐2.19 up ‐2.09
down 1.34 down 1.41
down 3.44 down 4.07
February 2014 August 2014
up ‐5.530 up ‐5.33
up ‐4.48 up ‐4.32
down 3.58 down 5.04
up ‐1.18 up ‐0.99
Divergent from D1 1.64 Divergent from I2 3.12
Divergent from D1 & Divergent from D3 ‐4.77b Divergent from D1 ‐2.49
down 1.43 down 1.80
up ‐1.01 Divergent from D3 ‐1.85
up ‐13.47 up ‐9.59
February 2013 August 2013
up ‐5.500 up ‐0.029
up ‐0.034 up ‐0.035
Monitor Well ID Aquifer Zone
Convergent on SFMW‐16up ‐2.39 1.52
down 1.38 down 1.56
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐2ES110514201639SPB PAGE 4 OF 4
011361
TABLE 3‐3Summary of Historical Groundwater Elevation, February 2002 through August 2014Fruit Avenue Plume Superfund SiteAlbuquerque, New Mexico
DM‐01 (S) DM‐02 (I1) DM‐03 (I1) DM‐04 (S) DM‐05 (S) DM‐06 (I1/I2) DM‐07 (I1/I2) DM‐13 (I2) DM‐13 (D1) HSM‐I2‐1 (I2) HSM‐I2‐4 (I2) HSM‐I2‐5 (I2) McDonalds (D2) MNW‐1 (I2) MNW‐12 (I2) MNW‐12 (D1) MNW‐12 (D2)Feb‐02 4915.54 4917.82 4918.63 4917.36 4915.81 4908.01 4908.7 4916.63 4921.26 ‐‐ ‐‐ ‐‐ 4900.48 ‐‐ ‐‐ ‐‐ ‐‐Oct‐04 4916.59 4918.03 4918.9 4917.45 4915.92 4907.29 4908.03 4917.79 4921.69 4920.72 4920.74 4918.44 4901.55 4926.35 ‐‐ ‐‐ ‐‐Apr‐05 4918.07 4919.37 4920.11 4918.81 4917.38 4909.62 4910.25 4919.12 4922.61 4922.03 4922.02 4919.85 4903.66 4927.2 4932.05 4932.01 4932.01Jul‐05 4917.66 4918.99 4919.76 4918.47 4916.98 4908.05 4908.98 4917.47 4922.11 4921.66 4921.64 4919.41 4898.98 4926.88 4931.69 4931.96 4931.6Feb‐06 4917.54 4918.83 4919.6 4918.3 4916.52 4909.55 4910.24 4918.63 4916.57 4921.52 4921.49 4919.45 4903.19 4926.69 4931.56 4931.61 4931.5Aug‐06 4916.84 4918.17 4918.98 4917.63 4916.13 4908.13 4908.79 ‐‐ ‐‐ 4920.89 4920.85 4918.73 4901.34 4926.25 4931.37 4931.43 4931.33Feb‐07 4917.67 4919.03 4919.76 4918.45 4917.01 4909.61 4910.28 ‐‐ ‐‐ 4921.69 4921.66 4919.68 4904.69 4926.79 4931.69 4931.63 4931.6Oct‐07 4917.03 4918.37 4919.16 4917.84 4916.35 4908.17 4909.02 ‐‐ ‐‐ 4921.05 4921.02 4918.9 4899.9 4926.31 4931.36 4931.32 4931.3Apr‐08 4918.23 4919.49 4920.31 4918.99 4917.55 4910.54 4911.33 4917.27 4919.24 4922.15 4922.12 4920.19 4904.75 4927.1 4931.82 4931.78 4931.77Oct‐08 4917.4 4918.74 4919.51 4918.22 4916.73 4908 4909.97 4916.39 4918.48 4921.43 4921.39 4919.29 4901.11 4926.61 4931.45 4931.48 4931.44Apr‐09 4917.85 4919.17 4919.84 4918.59 4917.17 4910.47 4911.32 4918.91 4922.25 4921.84 4921.79 4919.83 4903.99 4926.88 4931.66 4931.64 4931.58Oct‐09 4917.27 4918.65 4919.37 4918.06 4916.77 4910 4910.37 4916.28 4918.38 4921.34 4921.29 4919.17 4905.15 4926.74 4931.58 4931.55 4931.48Jan‐10 4918.17 4919.50 4920.03 4918.78 4917.36 4911.31 4912.06 4918.04 4919.23 4922.02 4922.10 4920.16 4907.85 4927.12 4931.68 4931.76 4931.70Aug‐10 4918.89 4920.12 4920.82 4919.64 4918.22 4912.23 4913.27 4919.93 4923.07 4922.72 4922.78 4920.90 4906.30 4927.61 4932.12 4932.16 4932.13Feb‐11 4919.84 ‐‐ ‐‐ ‐‐ ‐‐ 4913.63 4914.44 4920.78 4923.79 ‐‐ 4923.54 4921.77 4908.54 4928.15 4932.55 4932.52 4932.51Aug‐11 4919.71 ‐‐ ‐‐ ‐‐ 4919.04 4913.13 4913.94 4920.69 4923.66 ‐‐ ‐‐ 4921.72 4906.51 4928.12 4932.49 4932.53 4932.49Feb‐12 4920.29 ‐‐ ‐‐ ‐‐ 4919.65 4914.43 4915.23 4924.18 4921.20 ‐‐ 4924.02 4922.37 4910.33 4928.38 4932.62 4932.59 4932.58Aug‐12 4920.43 ‐‐ ‐‐ ‐‐ 4919.78 4914.14 4914.96 4921.34 4924.25 ‐‐ 4924.16 4922.45 4908.93 4928.54 4932.71 4932.75 4932.71Feb‐13 4920.88 ‐‐ ‐‐ ‐‐ 4920.22 4915.42 4915.96 4921.74 4924.68 ‐‐ 4924.60 4922.95 4912.19 4928.92 4933.12 4933.13 4933.12Aug‐13 4920.95 ‐‐ ‐‐ ‐‐ 4920.52 4915.15 4915.83 4922.00 4924.86 ‐‐ 4924.86 4922.22 4911.69 4929.09 4933.22 4933.21 4933.17Feb‐14 4921.93 ‐‐ ‐‐ ‐‐ 4921.31 4916.55 4917.12 4922.77 4925.55 ‐‐ 4925.58 4924.04 4914.35 4929.68 4933.64 4933.68 4933.64Aug‐14 4922.40 ‐‐ ‐‐ ‐‐ 4921.77 4916.88 4917.53 4923.17 4925.84 ‐‐ 4926.00 4924.50 4914.21 4929.96 4933.80 4933.83 4933.79
DM‐08 (I1/I2) DM‐09 (S) DM‐10 (S) DM‐11 (S) DM‐12 (I1/I2) DM‐13 (S) DM‐13 (I) MNW‐10 (I1) MNW‐10 (I2) MNW‐11 (I1) MNW‐11 (I2) MNW‐11 (D1) MNW‐11 (D2) MNW‐12 (I1) MNW‐14 (I2) MNW‐14 (D1) MNW‐14 (D2)Feb‐02 4909.02 4911.03 4909.39 4920.79 4921.82 4915.41 4916.52 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐Oct‐04 4908.26 4910.51 4908.56 4921.16 4922.38 4915.55 4916.41 4925.24 4925.25 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐Apr‐05 4910.49 4912.83 4911.54 4922.2 4923.21 4917.12 4917.89 4925.91 4925.94 4932.03 4932.07 4931.98 4932.23 4932.09 4923.62 4925.65 4926.02Jul‐05 4908.81 4911.83 4910.63 4921.89 4922.77 4916.68 4916.68 4925.48 4925.52 4931.6 4931.62 4931.54 4931.51 4931.74 4923.24 4925.18 4925.48Feb‐06 4910.36 4912.13 4911.35 4921.65 4922.65 4917.41 4919.51 4925.32 4925.32 4931.52 4931.55 4931.46 4931.45 4931.58 4923.1 4925.13 4925.52Aug‐06 4908.97 4911.23 4909.69 4921.15 4922.22 4915 ‐‐ 4924.89 4924.91 4931.4 4931.31 4931.25 4931.42 4931.39 4924.63 4925.13 4922.51Feb‐07 4910.60 4911 4911.38 4923.26 4921.49 4915 ‐‐ 4925.59 4925.59 4931.64 4931.67 4931.66 4931.59 4931.68 4923.23 4925.29 4925.68Oct‐07 4907.92 4911.37 4909.94 4921.31 4922.30 4915 ‐‐ 4924.95 4924.95 4931.32 4931.38 4931.21 4931.22 4931.39 4922.67 4924.69 4925.04Apr‐08 4911.35 4913.73 4912.29 4922.25 4923.20 4922.6 4918.07 4925.81 4925.81 4931.78 4931.77 4931.73 4931.69 4931.84 4923.68 4925.63 4925.98Oct‐08 4909.73 4912.12 4911.05 4921.60 4922.54 4916.41 4917.23 4925.09 4925.09 4931.37 4931.38 4931.29 4931.29 4931.54 4923.04 4924.99 4925.34Apr‐09 4911.21 4913.29 4912.10 4921.84 4922.86 4917.71 4916.90 4925.40 4925.40 4931.52 4931.59 4931.52 4931.47 4931.66 4923.39 4925.36 4925.75Oct‐09 4910.40 4912.31 4911.25 4921.38 4922.43 4917.18 4921.86 4924.89 4924.91 4931.37 4931.4 4931.44 4931.3 4931.54 4922.93 4924.93 4925.33Jan‐10 4912.50 4913.91 4912.69 4922.05 4923.12 4917.22 4922.61 4925.60 4925.60 4931.59 4931.63 4931.60 4931.57 4931.57 4923.65 4925.64 4926.05Aug‐10 4912.77 4915.02 4913.82 4922.64 4923.60 4917.98 4918.81 4926.06 4926.09 4931.99 4931.98 4931.96 4931.95 4932.15 4924.28 4926.12 4926.48Feb‐11 4914.38 4916.23 4914.93 4923.24 4924.22 4918.76 4919.68 4926.69 4926.71 4932.40 4932.42 4932.39 4932.36 4931.54 4924.93 4926.75 4927.13Aug‐11 4913.81 4916.10 4914.63 4923.26 4924.22 4919.59 4918.8 4926.74 4926.77 4932.39 4932.44 4932.42 4932.38 4932.52 4924.72 4926.71 4927.08Feb‐12 4915.45 4917.16 4915.61 4923.61 4924.60 4919.41 4920.19 4927.18 4927.21 4932.56 4932.58 4932.55 4932.54 4932.58 4925.32 4927.53 4927.10Aug‐12 4915.12 4917.16 4915.49 4923.77 4924.72 4919.50 4920.29 4927.30 4927.32 4932.65 4932.69 4932.62 4932.65 4932.76 4925.44 4927.23 4927.61Feb‐13 4916.37 4917.99 4916.38 4924.13 4925.15 4920.00 4920.75 4927.68 4927.73 4933.03 4933.07 4933.06 4933.00 4933.12 4925.82 4927.64 4928.05Aug‐13 4916.67 4918.09 4916.50 4924.37 4925.32 4920.26 4921.02 4927.85 4927.90 4933.12 4933.16 4933.13 4933.11 4933.22 4926.10 4927.83 4928.18Feb‐14 4917.33 4918.51 4917.55 4924.94 4925.95 4921.07 4921.83 4928.48 4928.51 4933.61 4933.62 4933.59 4933.57 4933.67 4926.75 4928.48 4928.88Aug‐14 4918.04 4919.78 4918.04 4925.27 4926.22 4921.52 4922.27 4928.75 4928.79 4933.73 4933.75 4933.73 4933.71 4933.82 4927.13 4928.76 4929.11
Note:‐‐ = Well not installed, abandoned, dry, or inaccessible
Date
Date
Well ID (Aquifer Zone)
Well ID (Aquifer Zone) Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐3ES110514201639SPB PAGE 1 OF 4
011362
TABLE 3‐3Summary of Historical Groundwater Elevation, February 2002 through August 2014Fruit Avenue Plume Superfund SiteAlbuquerque, New Mexico
Feb‐02Oct‐04Apr‐05Jul‐05Feb‐06Aug‐06Feb‐07Oct‐07Apr‐08Oct‐08Apr‐09Oct‐09Jan‐10Aug‐10Feb‐11Aug‐11Feb‐12Aug‐12Feb‐13Aug‐13Feb‐14Aug‐14
Feb‐02Oct‐04Apr‐05Jul‐05Feb‐06Aug‐06Feb‐07Oct‐07Apr‐08Oct‐08Apr‐09Oct‐09Jan‐10Aug‐10Feb‐11Aug‐11Feb‐12Aug‐12Feb‐13Aug‐13Feb‐14Aug‐14
Note:‐‐ = Well not installed, abandoned, dry, or inaccessible
Date
Date
MNW‐13 (D1) MNW‐13 (D2) MNW‐13 (D3) MNW‐13 (D4) MNW‐3 (D1) MNW‐3 (D2) MNW‐3 (D3) MNW‐4 (D1) MNW‐4 (D2) MNW‐4 (D3) MNW‐5 (D1) MNW‐8 (I1) MNW‐8 (I2) MNW‐9 (I1) MNW‐9 (I2) MNW‐9 (D1) MNW‐9 (D2) SFMW‐01 (S)‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4917.4‐‐ ‐‐ ‐‐ ‐‐ 4902.53 4900.7 4898.84 4888.43 4888.86 4889.25 4895.3 4926.75 4926.94 4928.65 4928.8 ‐‐ ‐‐ 4917.55
4892.84 4893.11 4893.71 4894.21 4904.74 4902.66 4900.71 4890.41 4890.35 4891.23 4897.21 4927.66 4927.88 4929.57 4929.59 4929.59 4929.59 4918.924884.46 4884.76 4885.25 4885.64 4901.09 4897.15 4893.57 4881.36 4881.64 4881.93 4890.29 4927.31 4927.55 4929.25 4929.24 4929.05 4929.18 4918.874893.95 4894.22 4894.75 4895.28 4904.72 4902.99 4901.32 4892.63 4892.94 4893.34 4898.19 4927.09 4927.3 4929.01 4929.04 4928.93 4929.07 4918.414890.84 4891.11 4891.66 4892.16 4902.77 4900.67 4898.65 4889.08 4889.36 4889.78 4895.23 4926.69 4926.9 4928.85 4929.01 4928.48 4928.51 4917.774895.11 4895.37 4895.86 4896.35 4905.43 4903.89 4901.88 4893.11 4893.37 4893.72 4898.88 4927.19 4927.39 4929.09 4929.15 4929.05 4929.25 4918.584888.24 4888.53 4889.09 4889.52 4902.04 4899.48 4897.23 4886.06 4886.36 4886.78 4893.21 4926.76 4926.97 4928.74 4928.78 4926.61 4928.75 4917.994893.72 4894.04 4894.72 4895.45 4905.89 4894.72 4902.55 4891.88 4892.28 4892.93 4898.32 4927.53 4927.7 4929.35 4929.39 4929.26 4929.41 4919.114889.27 4889.62 4890.31 4890.88 4903.54 4901.15 4898.05 4887.97 4888.34 4888.85 4894.64 4927.1 4927.28 4928.96 4928.99 4928.82 4928.95 4918.344894.21 4894.52 4895.19 4895.88 4906.01 4904.36 4902.93 4892.79 4893.15 4893.71 4898.58 4927.33 4927.54 4929.13 4929.18 4929.07 4929.21 4918.734895.61 4895.89 4896.5 4897.12 4906.22 4904.84 4903.62 4894.61 4894.92 4895.44 4899.72 4927.22 4927.41 4929 4929.04 4928.92 4929.07 4918.184899.68 4899.96 4900.58 4901.30 4907.53 4907.64 4906.91 4898.75 4899.06 4899.60 4903.19 4927.57 4928.08 4929.31 4929.35 4929.26 4929.41 4919.044896.73 4897.03 4897.71 4898.45 4908.59 4906.85 4905.41 4896.57 4895.96 4896.58 4901.14 4928.06 4928.23 4929.73 4929.77 4929.68 4929.84 4919.774900.51 4900.79 4901.85 4901.79 4910.39 4909.05 4907.94 4899.58 4899.88 4900.40 4904.17 4928.59 4928.78 4930.20 4930.25 4930.17 4930.33 4920.564896.00 4896.26 4897.04 4896.75 4908.78 4908.76 4905.14 4894.39 4894.8 4895.46 4900.87 4928.58 4928.76 4930.20 4930.23 4930.17 4930.30 4919.584903.02 4903.27 4903.91 4904.64 4911.66 4910.66 4909.89 4902.04 4902.34 4902.84 4906.41 4928.59 4928.78 4930.20 4930.25 4930.17 4930.33 ‐‐4899.87 4900.18 4900.87 4901.64 4909.02 4910.51 4907.79 4898.15 4898.53 4899.16 4904.19 4928.95 4929.11 4930.50 4930.55 4930.48 4930.64 4921.314905.58 4912.29 4906.34 4906.87 4913.06 4912.29 4911.63 4905.14 4905.38 4905.78 4908.58 4929.34 4929.50 4930.88 4930.95 4930.91 4931.02 4921.694901.92 4910.85 4902.64 4902.19 4911.35 4910.85 4909.55 4901.45 4901.78 4902.20 4906.08 4929.55 4929.71 4931.06 4931.11 4930.98 4931.13 4922.034907.30 4907.55 4908.03 4908.51 4914.70 4913.85 4913.11 4907.00 4906.94 4907.34 4910.35 4930.11 4930.27 4931.59 4931.65 4931.55 4931.71 4922.774906.42 4906.65 4907.15 4907.66 4914.78 4913.60 4912.64 4905.62 4905.88 4906.31 4909.81 4930.37 4930.57 4933.68 4931.88 4931.75 4931.91 4923.24
MNW‐15 (D1) MNW‐15 (D2) MNW‐15 (D3) MNW‐2 (I2) MNW‐5 (D2) MNW‐5 (D3) MNW‐5 (D4) MNW‐6 (D1) MNW‐6 (D2) MNW‐6 (D3) MNW‐7 (D4) SFMW‐02 (S) SFMW‐03 (S) SFMW‐04 (S) SFMW‐05 (S) SFMW‐06 (I1) SFMW‐07 (S) SFMW‐08 (S)‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4916.14 4915.52 4915.57 4915.24 4915.89 4918.44 ‐‐‐‐ ‐‐ ‐‐ 4923.4 4895.7 4895.97 ‐‐ 4898.28 4898.39 4898.44 4894.15 4915.94 4915.52 4915.63 4915.38 4916.02 4918.58 ‐‐‐‐ ‐‐ ‐‐ 4921.57 4897.58 4897.86 4897.35 4900.47 4900.58 4900.56 4895.02 4917.41 4917.08 4917.2 4916.82 4917.52 4919.92 ‐‐‐‐ ‐‐ ‐‐ 4921.04 4890.66 4891.53 4889.72 4894.9 4894.87 4894.59 4885.47 4917.01 4916.62 4916.74 4916.41 4917.04 4919.64 ‐‐
4880.43 4889.64 4889.85 4921 4898.28 4898.49 4898.35 4900.59 4900.61 4900.65 4897.14 4916.89 4916.58 4916.68 4916.17 4916.97 4919.45 ‐‐4878.55 4886.09 4886.24 4920.38 4895.61 4895.81 4895.26 4898.39 4898.39 4898.38 4893.58 4916.17 4915.79 4915.89 4915.62 4916.23 4919.05 ‐‐4881.37 4890.82 4891.03 4921.26 4899.29 4899.5 4898.96 4901.78 4901.85 4901.94 4896.96 4917.02 4916.69 4915 4916.5 4917.13 4919.52 ‐‐4878.43 4882.99 4883.14 4920.45 4893.58 4893.85 4893.25 4896.81 4896.83 4896.68 4891.51 4916.38 4915.99 4916.09 4915.83 4916.46 4918.97 ‐‐4879.62 4888.59 4888.89 4921.57 4898.76 4899.02 4899.4 4901.41 4901.49 4901.61 4898.62 4917.57 4917.32 4917.46 4917.03 4917.67 4920.07 4921.784875.95 4884.10 4884.24 4920.71 4895.05 4895.27 4895.1 4897.99 4897.97 4897.95 4894.51 4916.74 4916.4 4916.54 4916.18 4916.82 4919.38 ‐‐4878.98 4889.48 4889.72 4921.22 4898.97 4899.22 4899.74 4901.39 4901.43 4901.50 4899.33 4916.58 4916.92 ‐‐ 4916.95 4917.29 4919.76 ‐‐4878.66 4891.15 4891.4 4920.63 4900.11 4900.36 4900.67 4902.21 4902.31 4902.52 4900.51 4916.62 4916.32 4916.46 4916.07 4916.7 4919.24 ‐‐4881.64 4896.00 4896.27 4921.54 4903.60 4903.87 4903.57 4905.28 4905.46 4905.78 4904.32 4917.39 4917.30 4917.48 4917.00 4917.63 4920.03 ‐‐4881.95 4892.14 4892.50 4922.16 4901.52 4901.73 4902.31 4903.79 4903.79 4903.87 4902.15 4918.26 4918.07 4918.23 4917.71 4918.38 4920.73 4922.154885.05 4896.68 4896.90 ‐‐ 4904.52 4904.74 4905.33 4906.39 4906.44 4906.50 4902.15 ‐‐ 4919.03 ‐‐ ‐‐ ‐‐ 4921.41 4923.774833.10 4890.77 4891.09 4917.98 4901.16 4901.37 4901.92 4903.8 4903.78 4903.82 4901.37 ‐‐ 4918.87 ‐‐ ‐‐ ‐‐ 4921.42 ‐‐4886.96 4899.50 4900.06 4923.59 4907.76 4906.96 4907.73 4908.50 4908.55 4908.69 ‐‐ ‐‐ 4919.50 ‐‐ ‐‐ ‐‐ 4921.844885.12 4895.10 4895.43 4923.68 4904.25 4904.47 4905.22 4906.57 4906.58 4906.65 4904.58 ‐‐ 4919.60 ‐‐ ‐‐ ‐‐ 4921.99 ‐‐4889.13 4902.60 4902.83 4924.20 4908.90 4909.09 4909.59 ‐‐ ‐‐ ‐‐ 4909.39 ‐‐ 4920.11 ‐‐ ‐‐ ‐‐ 4922.374888.72 4898.02 4898.31 4923.50 4906.44 4906.65 4904.59 4908.45 4908.54 4908.64 4906.68 ‐‐ 4920.38 ‐‐ ‐‐ ‐‐ 4922.68 ‐‐4892.54 4904.28 4904.52 4925.02 4910.65 4911.15 4911.04 4912.16 4912.30 4912.45 4910.77 ‐‐ 4921.23 ‐‐ ‐‐ ‐‐ 4923.35 ‐‐4893.05 4902.97 4903.15 4925.68 4910.11 4910.30 4910.38 4911.88 4911.99 4912.08 4909.98 ‐‐ 4921.72 ‐‐ ‐‐ ‐‐ 4923.78 ‐‐
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐3ES110514201639SPB PAGE 2 OF 4
011363
TABLE 3‐3Summary of Historical Groundwater Elevation, February 2002 through August 2014Fruit Avenue Plume Superfund SiteAlbuquerque, New Mexico
Feb‐02Oct‐04Apr‐05Jul‐05Feb‐06Aug‐06Feb‐07Oct‐07Apr‐08Oct‐08Apr‐09Oct‐09Jan‐10Aug‐10Feb‐11Aug‐11Feb‐12Aug‐12Feb‐13Aug‐13Feb‐14Aug‐14
Feb‐02Oct‐04Apr‐05Jul‐05Feb‐06Aug‐06Feb‐07Oct‐07Apr‐08Oct‐08Apr‐09Oct‐09Jan‐10Aug‐10Feb‐11Aug‐11Feb‐12Aug‐12Feb‐13Aug‐13Feb‐14Aug‐14
Note:‐‐ = Well not installed, abandoned, dry, or inaccessible
Date
Date
SFMW‐09 (I1) SFMW‐10 (I2) SFMW‐11 (S) SFMW‐12 (I1) SFMW‐13 (I2) SFMW‐14 (D1) SFMW‐15 (S) SFMW‐23 (D2) SFMW‐24 (S) SFMW‐25 (I1/I2) SFMW‐26 (I2) SFMW‐27 (I2) SFMW‐28 (I2) SFMW‐29 (I2) SFMW‐37 (I2)‐‐ 4920.35 4923.31 4923.24 4923.3 4923.42 ‐‐ 4901.25 4912.88 4911.2 4910.62 ‐‐ 4919.02 ‐‐ ‐‐
4921.59 4922.03 4924.96 4923.97 4923.98 4924.12 4913.13 4900.11 4912.6 4910.84 4910.22 4916.47 4919.22 4912.52 ‐‐4922.45 4922.83 4924.62 4924.64 4924.65 4924.81 4914.86 4902.74 4914.34 4912.69 4912.09 4923.39 4920.44 4914.28 4896.164922.04 4922.37 4924.28 4924.29 4924.31 4924.37 4914.26 4898.26 4913.68 4911.63 4911.01 4922.96 4920.12 4913.44 4904.214921.6 4922.27 4924.11 4924.1 4924.14 4924.27 4914.42 4902.32 4913.97 4912.42 4911.89 4922.88 4919.99 4913.89 4907.5
4921.42 4921.8 4923.72 4923.71 4923.73 4923.86 4913.86 4900.75 4912.98 4911.28 4910.68 4922.39 4919.28 4912.71 4906.614922.14 4922.5 4924.32 4924.31 4924.34 4924.46 4914.65 4903.09 4914.04 4912.53 4911.97 4923.01 ‐‐ 4913.94 4906.464921.53 4921.87 4923.83 4923.81 4923.85 4923.9 4913.75 4899.54 4913.05 4911.34 4910.72 4922.45 4919.37 4912.85 4907.344922.49 4922.78 4924.58 4924.57 4924.59 4924.69 4915.27 4903.48 4914.85 4913.3 4912.77 4923.33 4921.17 4914.65 4907.324921.74 4922.08 4924.02 4924.01 4924.02 4924.06 ‐‐ 4900.77 4913.8 4912.08 4911.57 4922.75 4919.88 4913.67 4907.494922.05 4922.41 4924.19 4924.19 4924.22 4924.33 ‐‐ 4903.30 4914.60 4913.15 4912.64 4923.10 4920.33 4914.56 4909.434921.57 4921.94 4923.97 4923.97 4924 4924.09 ‐‐ 4903.59 4914.09 4912.57 4912.06 4922.71 4919.89 4914.02 4906.654922.27 4922.66 4924.34 4924.37 4924.40 4924.56 4915.31 4906.00 4915.04 4913.74 4913.27 4923.37 4920.67 4915.09 4908.424922.80 4923.14 4924.81 4924.84 4924.87 4924.98 4916.17 4905.56 4915.95 4914.68 4914.22 4923.86 4921.26 4916.09 4911.894923.44 4922.76 4925.35 4925.39 4925.44 4925.58 4917.16 4907.57 4916.95 4925.78 4915.37 4924.47 4921.99 4916.98 4913.45
‐‐ 4923.78 4925.34 4925.38 4925.40 4925.55 4917.07 4905.86 4916.77 4915.49 4915 4924.43 4921.92 ‐‐ 4912.08‐‐ 4924.22 4925.65 4925.69 4925.74 4925.92 4917.72 4909.07 4917.59 4916.51 4916.14 4923.78 4922.30 ‐‐ 4913.69‐‐ 4924.33 4925.79 4926.19 4925.86 4926.02 4917.93 4907.92 4927.55 4916.37 4915.97 4924.92 4922.44 ‐‐ 4913.15‐‐ 4924.78 4926.15 4926.19 4926.24 4926.42 4918.61 4910.45 4918.25 4917.23 4916.87 4925.33 4922.91 ‐‐ 4913.00‐‐ 4924.94 4926.35 4926.38 4926.42 4926.58 4919.77 4909.00 4918.36 4917.26 4916.80 4925.54 4923.19 ‐‐ 4912.61‐‐ 4925.57 4926.89 4926.93 4926.98 4927.17 4919.84 4912.24 4919.32 4918.34 4917.98 4926.16 4923.80 ‐‐ 4914.36‐‐ 4925.84 4927.11 4927.16 4927.18 4927.39 4920.34 4912.26 4919.80 4918.78 4918.39 4926.44 ‐‐ ‐‐ 4914.75
SFMW‐16 (I1) SFMW‐17 (I2) SFMW‐18 (I1) SFMW‐19 (I2) SFMW‐20 (I1) SFMW‐21 (I2) SFMW‐22 (D1) SFMW‐30(I2) SFMW‐31 (I2) SFMW‐32 (I2) SFMW‐33 (D2) SFMW‐34 (D4) SFMW‐35 (D3) SFMW‐36 (D4) SFMW‐44 (D2)‐‐ 4916.55 ‐‐ 4919.29 4901.3 4900.45 4901.75 ‐‐ ‐‐ 4892.26 ‐‐ 4899.25 4899.64 4898.09 4894.04
4914.33 4915.66 4919.34 4919.63 4899.29 4899.46 4900.53 4909.02 4890.75 4891.07 4904.55 4897.81 4898.36 4896.55 4895.764916.03 4918.14 4920.54 ‐‐ 4901.7 4902 4902.74 4911.21 4892.97 4893.33 4906.73 4899.57 4900.32 4898.41 4897.864915.59 4917.69 4920.22 ‐‐ 4900.7 4900.85 4899.37 4910.43 4892.67 4893.02 4904.12 4892.95 4894.85 4891.48 4891.914915.63 4917.64 4920.05 ‐‐ 4901.35 4901.69 4902.73 4910.82 4892.49 4892.84 4907.28 4900.1 4901.2 4898.93 4897.754914.88 4916.98 4919.4 ‐‐ 4900.28 4900.55 4901.05 4909.44 4891.83 4892.08 4905.51 4897.64 4899.07 4896.44 4895.484915.83 4917.86 4920.14 ‐‐ 4902.06 4902.36 4903.45 4910.78 4893.33 4893.98 4906.98 4900.63 4901.39 4899.66 4899.174915.14 4917.11 4919.59 ‐‐ 4900.64 4900.81 4899.29 4909.91 4892.5 4892.67 4905.39 4896.36 4896.76 4894.92 4893.724916.46 4918.33 4920.64 ‐‐ 4903.23 4903.48 4903.92 4911.71 4894.34 4894.76 4907.96 4901.34 4900.73 4900.06 4899.024915.41 4917.44 4919.96 ‐‐ 4902.6 4901.79 4901.44 4910.55 4892.84 4893.27 4905.9 4898.43 4899.36 4896.42 4895.154916.03 4917.94 4920.34 ‐‐ 4902.90 4903.18 4903.78 4911.66 4893.72 4894.27 4908.25 4901.64 4902.58 4900.36 4898.61
‐‐ ‐‐ 4919.87 ‐‐ 4902.11 4902.43 4903.82 4911.09 4892.94 4893.58 4907.46 4901.9 4902.19 4900.94 4899.944916.42 4918.30 4920.61 ‐‐ 4903.68 4904.06 4906.08 4912.59 4894.13 4894.85 4909.32 4905.43 4905.06 4898.28 4903.064917.20 4918.96 4921.25 ‐‐ 4905.87 4906.10 4906.12 4913.60 4896.62 4897.88 4910.24 4903.96 4904.75 4902.73 4901.064918.13 4919.80 4921.91 ‐‐ 4907.07 4907.36 4908.01 ‐‐ 4897.92 4989.98 4911.80 4906.40 4907.01 4905.40 4903.574918.06 4919.78 4921.92 ‐‐ 4906.78 4905.93 4906.60 ‐‐ 4898.25 4899.12 4910.73 4903.87 4904.78 4902.56 4900.974918.81 4920.39 4922.33 ‐‐ 4908.17 4908.46 4909.41 ‐‐ 4909.16 4900.33 ‐‐ ‐‐ 4907.80 4907.48 4905.594918.48 4919.52 4922.47 ‐‐ 4908.15 4908.35 4908.43 ‐‐ 4899.76 4900.55 4912.24 4906.48 4907.16 4905.40 4903.734919.43 4921.00 4922.85 ‐‐ 4909.28 4909.60 4910.75 ‐‐ 4909.16 4901.70 ‐‐ 4910.03 4909.78 4909.11 4907.804919.72 4921.24 4923.14 ‐‐ 4909.68 4909.85 4909.49 ‐‐ 4901.86 4902.88 4912.88 4907.84 4908.07 4906.73 4906.164920.62 4922.03 4923.79 ‐‐ 4911.31 4911.50 4912.39 ‐‐ 4903.56 4904.65 4914.87 4911.43 4911.30 4910.58 4910.094921.07 4922.43 4924.16 ‐‐ 4912.06 4912.23 4912.58 ‐‐ 4904.82 4905.84 4915.06 4910.99 4911.09 4910.11 4909.51
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐3ES110514201639SPB PAGE 3 OF 4
011364
TABLE 3‐3Summary of Historical Groundwater Elevation, February 2002 through August 2014Fruit Avenue Plume Superfund SiteAlbuquerque, New Mexico
Feb‐02Oct‐04Apr‐05Jul‐05Feb‐06Aug‐06Feb‐07Oct‐07Apr‐08Oct‐08Apr‐09Oct‐09Jan‐10Aug‐10Feb‐11Aug‐11Feb‐12Aug‐12Feb‐13Aug‐13Feb‐14Aug‐14
Feb‐02Oct‐04Apr‐05Jul‐05Feb‐06Aug‐06Feb‐07Oct‐07Apr‐08Oct‐08Apr‐09Oct‐09Jan‐10Aug‐10Feb‐11Aug‐11Feb‐12Aug‐12Feb‐13Aug‐13Feb‐14Aug‐14
Note:‐‐ = Well not installed, abandoned, dry, or inaccessible
Date
Date
SFMW‐38 (D1) SFMW‐39 (D2) SFMW‐40 (D3) SFMW‐41 (D3/D4) SFMW‐42 (I1) SFMW‐43 (I1) WB‐01 (S) WB‐01 (I1/I2) WB‐02 (S) WB‐02 (I1/I2)4896.6 4896.45 4895.58 4894.29 ‐‐ ‐‐ 4925.27 ‐‐ 4896.45 ‐‐
4895.33 4895.18 4894.25 4893.33 4905.96 4890.01 4924.05 4924.34 4895.18 4925.714897.49 4897.28 4896.2 4895.11 4908.7 4892.2 4924.76 4925.22 4897.28 4926.54
4893 4892.34 4890.18 4888.14 4907.51 4892.03 4924.7 4924.85 4892.34 4926.24897.27 4896.26 4896.37 4895.71 4908.29 4891.77 4924.43 4924.65 4896.26 49264895.3 4894.23 4894.1 4893.12 4906.76 4891.11 4924.03 4924.25 4894.23 4925.61
4898.51 4898.35 4897.37 4896.44 4908.68 4892.65 4924.56 4924.82 4898.35 4926.134894.09 4892.85 4892.59 4891.47 4906.91 4891.71 4924.15 4924.35 4892.85 4925.714898.72 4898.55 4897.63 4896.77 4909.68 4893.49 4924.89 4925.1 4898.55 4926.384895.44 4894.3 4894.13 4893.09 4908.25 4891.92 4924.86 4924.07 4894.3 4925.884898.30 4897.28 4897.60 4897.04 4909.69 4892.77 4924.59 4924.80 4897.28 4926.104899.15 4899.13 4898.42 4897.79 4909.16 4892.05 4924.46 4924.66 4899.13 4925.754901.78 4901.90 4901.47 4901.11 4910.48 4893.29 4924.8 4925.05 4901.90 4926.304900.78 4899.70 4900.04 4899.25 4912.03 4895.73 4925.26 4925.50 4899.70 4926.734902.97 4901.95 4902.49 4902.13 4912.89 4897.16 ‐‐ 4926.05 4901.95 4927.294900.91 4899.79 4899.93 4899.23 4897.45 4900.97 ‐‐ 4926.09 ‐‐ 4927.264904.54 4903.69 4904.32 4904.13 ‐‐ 4898.71 ‐‐ 4926.34 ‐‐ 4927.514903.47 4902.23 4902.52 4902.04 ‐‐ 4898.98 ‐‐ 4926.50 ‐‐ 4927.654906.47 4906.10 4906.14 4905.94 ‐‐ 4900.02 ‐‐ 4926.89 ‐‐ 4928.054905.37 4905.21 4904.43 4903.69 ‐‐ 4901.37 ‐‐ 4927.07 ‐‐ 4928.204908.33 4908.30 4907.87 4907.48 ‐‐ 4903.13 ‐‐ 4927.62 ‐‐ 4928.764908.28 4908.19 4907.59 4907.03 ‐‐ 4904.52 ‐‐ 4927.86 ‐‐ 4928.96
SFMW‐45 (D2) SFMW‐46 (D1/D2) SFMW‐47 (I1/I2) SPSC‐MW19 (S) SPSC‐MW5 (S) SPSC‐W13 (S)4892.77 4888.35 4915.56 4902.11 ‐‐ ‐‐4894.56 4890.56 4916.01 4901.07 ‐‐ ‐‐4896.41 4892.36 4917.49 4903.76 4909.15 ‐‐4890.27 4884.69 4917.03 4902.66 ‐‐ ‐‐4891.25 4893.7 4917 4903.45 4903.63 4903.454894.59 4890.76 4916.27 4904.1 4903.11 49054897.85 4894.44 4917.2 4904.06 4909.46 4904.094892.97 4888.64 4916.38 4902.54 4908.14 4902.624898.01 4893.87 4917.77 4905.26 4910.84 4905.214894.92 4890.06 4916.86 4903.55 4909.18 4903.74898.35 4894.34 4917.40 4904.96 4910.70 4905.104899.23 4895.65 4916.79 4904.11 4909.61 4904.244902.28 4899.60 4917.86 4905.71 4911.30 4906.024901.06 4897.01 4918.50 4907.66 4913.23 4908.124903.70 4900.35 4919.36 4908.97 4914.46 4909.874900.20 4896.35 4919.30 4908.64 4911.97 4908.384905.23 4902.28 4919.95 4910.03 4915.26 4909.684903.31 4899.62 4920.03 4919.89 4915.31 ‐‐4907.47 4904.99 4921.54 4911.32 4916.13 ‐‐4905.76 4902.24 4920.80 4911.23 4916.11 ‐‐4909.14 4906.67 4921.63 4914.76 4917.50 ‐‐4908.78 4905.98 4922.07 4913.55 4918.06 4912.67
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
Well ID (Aquifer Zone)
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐3ES110514201639SPB PAGE 4 OF 4
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TABLE 3‐4Summary of Chlorinated VOCs Detected in Groundwater, August 25, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
cis‐1,2‐ DCE PCEtrans‐1,2‐
DCE TCEVinyl
Chloride
70 5 100 5 1**HSM‐I2‐5 I2 HSM‐I2‐5‐17‐0814‐FD HSM‐I2‐5‐17 08/25/2014 09:57:00 PDB GW ug/L 6.4 = 0.5 U 1.0 = 25.5 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐0814 HSM‐I2‐5‐17 08/25/2014 08:57:00 PDB GW ug/L 6.9 = 0.5 U 1.1 = 26.0 = 0.5 UHSM‐I2‐5
McDonalds (D2) D2 McDonalds‐D2‐5‐0814 McDonalds‐D2‐5 08/25/2014 08:25:00 PDB GW ug/L 0.8 = 0.5 U 0.5 U 5.0 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐8‐0814 McDonalds‐D2‐8 08/25/2014 08:20:00 PDB GW ug/L 0.9 = 0.5 U 0.5 U 5.1 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐2‐0814 McDonalds‐D2‐2 08/25/2014 08:28:00 PDB GW ug/L 0.8 = 0.5 U 0.5 U 6.3 = 0.5 UMcDonalds (D2)
MNW‐1 (I2) I2 MNW‐1‐I2‐7‐0814 MNW‐1‐I2‐7 08/25/2014 08:15:00 PDB GW ug/L 4.3 = 0.5 U 1.3 = 19.7 = 0.5 UMNW‐1 (I2)
MNW‐11 (D1) D1 MNW‐11‐D1‐2‐082014 MNW‐11‐D1‐2‐0 08/25/2014 12:24:00 PDB GW ug/L 11.3 = 0.5 U 12.8 = 29.0 = 0.5 UMNW‐11 (D1)MNW‐14 (D1) D1 MNW‐14‐D1‐7‐0814 MNW‐14‐D1‐7 08/25/2014 09:56:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 1.6 = 0.5 UMNW‐14 (D1)MNW‐14 (I2) I2 MNW‐14‐I2‐8‐0814 MNW‐14‐I2‐8 08/25/2014 09:50:00 PDB GW ug/L 8.1 = 0.5 U 1.1 = 39.3 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐0814‐FD MNW‐14‐I2‐2 08/25/2014 10:48:00 PDB GW ug/L 7.9 = 0.5 U 1.2 = 44.2 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐0814 MNW‐14‐I2‐2 08/25/2014 09:48:00 PDB GW ug/L 7.9 = 0.5 U 1.3 = 44.8 = 0.5 UMNW‐14 (I2)MNW‐4 (D2) D2 MNW‐4‐D2‐7‐0814 MNW‐4‐D2‐7 08/25/2014 11:05:00 PDB GW ug/L 3.4 = 0.5 U 0.7 = 3.1 = 0.5 UMNW‐4 (D2)MNW‐5 (D1) D1 MNW‐5‐D1‐12‐0814 MNW‐5‐D1‐12 08/25/2014 09:19:00 PDB GW ug/L 3.1 = 0.5 U 1.3 = 3.6 = 0.5 UMNW‐5 (D1) D1 MNW‐5‐D1‐7‐0814 MNW‐5‐D1‐7 08/25/2014 09:15:00 PDB GW ug/L 5.6 = 1.4 = 2.3 = 9.7 = 0.5 UMNW‐5 (D1)MNW‐5 (D2) D2 MNW‐5‐D2‐7‐0814 MNW‐5‐D2‐7 08/25/2014 09:55:00 PDB GW ug/L 8.8 = 0.9 = 3.6 = 14.9 = 0.5 UMNW‐5 (D2)MNW‐5 (D3) D3 MNW‐5‐D3‐17‐0814‐FD MNW‐5‐D3‐17 08/25/2014 09:30:00 PDB GW ug/L 9.8 = 0.5 U 6.4 = 16.2 = 0.5 UMNW‐5 (D3) D3 MNW‐5‐D3‐17‐0814 MNW‐5‐D3‐17 08/25/2014 09:28:00 PDB GW ug/L 9.9 = 0.5 U 6.1 = 16.4 = 0.5 UMNW‐5 (D3)MNW‐8 (I2) I2 MNW‐8‐I2‐7‐0814 MNW‐8‐I2‐7 08/25/2014 08:04:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐8 (I2)MNW‐9 (D1) D1 MNW‐9‐D1‐2‐0814‐FD MNW‐9‐D1‐2 08/25/2014 13:47:00 PDB GW ug/L 1.4 = 0.5 U 1.6 = 2.5 = 0.5 UMNW‐9 (D1) D1 MNW‐9‐D1‐2‐0814 MNW‐9‐D1‐2 08/25/2014 12:47:00 PDB GW ug/L 1.3 = 0.5 U 1.0 = 3.6 = 0.5 UMNW‐9 (D1)MNW‐9 (I2) I2 MNW‐9‐I2‐17‐0814 MNW‐9‐I2‐17 08/25/2014 12:37:00 PDB GW ug/L 1.4 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐9 (I2)
SFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐0814 SFMW‐14‐D1‐2 08/25/2014 08:27:00 PDB GW ug/L 1.0 = 0.5 U 0.6 = 18.8 = 0.5 USFMW‐14 (D1)SFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐0814 SFMW‐17‐I2‐8 08/25/2014 09:14:00 PDB GW ug/L 3.8 = 0.5 U 3.2 = 5.6 = 0.5 USFMW‐17 (I2)
Matrix UnitRemediation Goals (MCLs) μg/L
Station IDAquiferZone* Sample ID Location Date Collected
Sampling Method
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐4ES110514201639SPB PAGE 1 OF 2
011366
TABLE 3‐4Summary of Chlorinated VOCs Detected in Groundwater, August 25, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
cis‐1,2‐ DCE PCEtrans‐1,2‐
DCE TCEVinyl
Chloride
70 5 100 5 1**Matrix UnitRemediation Goals (MCLs) μg/L
Station IDAquiferZone* Sample ID Location Date Collected
Sampling Method
SFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐0814 SFMW‐18‐I1‐8 08/25/2014 10:03:00 PDB GW ug/L 1.1 = 0.5 U 0.5 U 2.4 = 0.5 USFMW‐18 (I1)SFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐0814 SFMW‐20‐I1‐5 08/25/2014 12:25:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐20 (I1)SFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐0814 SFMW‐21‐I2‐12 08/25/2014 12:08:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐0814 SFMW‐21‐I2‐17 08/25/2014 12:12:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2)SFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐0814 SFMW‐22‐D1‐8 08/25/2014 12:38:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1)SFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐0814 SFMW‐23‐D2‐5 08/25/2014 12:30:00 PDB GW ug/L 3.8 = 0.5 U 0.7 = 10.6 = 0.5 USFMW‐23 (D2)SFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐0814 SFMW‐25‐I1‐5 08/25/2014 13:19:00 PDB GW ug/L 3.3 = 0.5 U 0.7 = 7.9 = 0.5 USFMW‐25 (I1)SFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐0814 SFMW‐26‐I2‐2 08/25/2014 13:08:00 PDB GW ug/L 1.1 = 0.5 U 0.5 U 2.5 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐0814 SFMW‐26‐I2‐8 08/25/2014 13:09:00 PDB GW ug/L 1.2 = 0.5 U 0.5 U 2.6 = 0.5 USFMW‐26 (I2)SFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐0814 SFMW‐27‐I2‐8 08/25/2014 10:18:00 PDB GW ug/L 6.1 = 0.5 U 4.3 = 14.5 = 0.5 USFMW‐27 (I2)SFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐0814 SFMW‐35‐D3‐5 08/25/2014 12:00:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3)
SFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐0814 SFMW‐41‐D3/D4‐5 08/25/2014 11:20:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐41 (D3/D4)
SFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐0814 SFMW‐44‐D2‐17 08/25/2014 08:50:00 PDB GW ug/L 6.8 = 0.9 = 2.7 = 13.1 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐0814 SFMW‐44‐D2‐12 08/25/2014 08:55:00 PDB GW ug/L 7.6 = 1.1 = 3.0 = 14.3 = 0.5 USFMW‐44 (D2)
SFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2‐0814 SFMW‐46‐D1/D2‐2 08/25/2014 10:48:00 PDB GW ug/L 1.2 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐46 (D1/D2)SFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐0814 SFMW‐47‐I1/I2‐12 08/25/2014 08:44:00 PDB GW ug/L 5.8 = 0.5 U 1.0 = 22.6 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐0814 SFMW‐47‐I1/I2‐22 08/25/2014 08:46:00 PDB GW ug/L 6.2 = 0.5 U 0.9 = 25.2 = 0.5 USFMW‐47 (I1/I2)
Notes:µg/L = microgram per liter J = estimated concentrationDCE = dichloroethylene UJ = not detected, estimated concentration ‐ resulting from improper temperature or holding time exceedanceDL = diluted sample; used as suffix to Sample ID L = Reported concentration is below the Contract Required Quantitation LimitGW = groundwaterMCL = maximum contaminant level M = Reported concentration should be used as a raised quantitation limit because of interferences and/or laboratory contamination.PCE = perchloroethylene (tetrachloroethylene) * = See Long‐term Monitoring Plan (included in Volume 1 of the 100% Remedial Design) for description of the aquifer zones.PDB = passive diffusion bag ** = The Record of Decision does not list a remediation goal for vinyl chloride. Value is the NMED drinking water standard.TCE = trichloroethylene Bold = detected resultU = not detected= = detected concentration
^ = High biased (actual concentration may be lower than the reported)
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐4ES110514201639SPB PAGE 2 OF 2
011367
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2b
AML (Elite) supply unknown FR844 NA 5/13/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FR846 NA 5/13/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FW851 NA 9/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FW852 NA 9/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FW853 NA 9/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
Atomic‐MW1 unknown NA 5/10/2020 0:00 unknownAtomic‐MW1 unknown FEF87 NA 8/12/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
COKE Supply unknown NA 5/10/2020 0:00 unknownCOKE Supply unknown FAR03 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 1 = 10 = 1 UCOKE Supply unknown FAR01 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 1 = 11 = 1 UCOKE Supply unknown FAR02 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 1 = 11 = 1 UCOKE Supply unknown FAR04 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 2 = 11 = 1 UCOKE Supply unknown FAQ98 NA 8/23/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 12 = 1 UCOKE Supply unknown FAQ99 NA 8/23/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 13 = 1 UCOKE Supply unknown FAR00 NA 8/23/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 13 = 1 UCOKE Supply unknown FW818 NA 8/11/1997 0:00 unknown GW µg/L 1 = 1 U 1 U 1 = 1 UCOKE Supply unknown FW817 NA 8/11/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UCOKE Supply unknown FW821 NA 8/11/1997 0:00 unknown GW µg/L 3 = 1 U 1 = 5 = 1 UCOKE Supply unknown FW820 NA 8/11/1997 0:00 unknown GW µg/L 4 = 1 U 1 = 11 = 1 UCOKE Supply unknown FW819 NA 8/11/1997 0:00 unknown GW µg/L 4 = 1 U 2 = 11 = 1 UCOKE Supply unknown FW815 NA 8/11/1997 0:00 unknown GW µg/L 5 U 5 U 5 U 5 U 5 UCOKE Supply unknown FW816 NA 8/11/1997 0:00 unknown GW µg/L 5 U 5 U 5 U 5 U 5 UCOKE Supply unknown not assigned‐21 NA 7/7/1989 0:00 unknown GW µg/L 2.4 = T 1.2 = 13.1 =COKE Supply unknown not assigned‐4 NA 7/7/1989 0:00 unknown GW µg/L 2.4 = T 1.2 = 13.1 =COKE Supply unknown not assigned‐20 NA 4/25/1989 0:00 unknown GW µg/L 7 = 14.5 =COKE Supply unknown not assigned‐3 NA 4/25/1989 0:00 unknown GW µg/L 7 = ND ND 14.5 =COKE Supply unknown not assigned‐2 NA 8/20/1987 0:00 unknown GW µg/L ND ND ND NDCOKE Supply unknown not assigned‐18 NA 12/3/1986 0:00 unknown GW µg/L TCOKE Supply unknown not assigned‐1 NA 12/3/1986 0:00 unknown GW µg/L ND T ND ND
Conv. Center unknown NA 5/10/2020 0:00 unknownConv. Center unknown not assigned‐36 NA 1/18/1989 0:00 unknown GW µg/L 14 = 4 = 2.6 =Conv. Center unknown not assigned‐14 NA 1/18/1989 0:00 unknown GW µg/L 14 = ND 4 = 2.6 =Conv. Center unknown not assigned‐35 NA 4/28/1988 0:00 unknown GW µg/L 25 = 14 = 4 =Conv. Center unknown not assigned‐13 NA 4/28/1988 0:00 unknown GW µg/L 25 = ND 14 = 4 =Conv. Center unknown not assigned‐34 NA 2/12/1988 0:00 unknown GW µg/L 30 = 22 = 2 =Conv. Center unknown not assigned‐12 NA 2/12/1988 0:00 unknown GW µg/L 30 = ND 22 = 2 =
D2E‐P1 (D2) NA 5/10/2020 0:00 unknownD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 6/16/14 Grab GW µg/L 1.0 = 0.5 U 0.5 U 2.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 6/16/14 Grab GW µg/L 1.0 = 0.5 U 0.5 U 2.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 3/18/14 Grab GW µg/L 1.0 = 0.5 U 0.5 U 2.4 = 0.5 U
Matrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 1 OF 72
011368
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
D2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 3/18/14 Grab GW µg/L 1.0 = 0.5 U 0.5 U 2.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 2/17/14 Grab GW µg/L 1.0 = 0.5 U 0.5 U 2.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 2/17/14 Grab GW µg/L 0.9 = 0.5 U 0.5 U 2.4 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 1/20/14 Grab GW µg/L 1.0 = 0.5 U 0.5 U 2.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 1/20/14 Grab GW µg/L 1.0 = 0.5 U 0.5 U 2.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 12/16/13 Grab GW µg/L 1.1 = 0.5 U 0.5 U 2.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 12/16/13 Grab GW µg/L 1.1 = 0.5 U 0.5 U 3 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 11/19/13 Grab GW µg/L 1.1 = 0.5 U 0.5 U 2.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 11/19/13 Grab GW µg/L 1.1 = 0.5 U 0.5 U 2.8 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 10/28/13 Grab GW µg/L 1.1 = 0.5 U 0.5 U 2.7 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 10/28/13 Grab GW µg/L 1.1 = 0.5 U 0.5 U 2.7 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 9/25/13 Grab GW µg/L 1.2 = 0.5 U 0.5 U 3.1 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 9/25/13 Grab GW µg/L 1.2 = 0.5 U 0.5 U 3.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 8/14/13 Grab GW µg/L 0.9 = 0.5 U 0.5 U 2.3 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 8/14/13 Grab GW µg/L 0.8 = 0.5 U 0.5 U 2.3 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 7/15/13 Grab GW µg/L 1.2 = 0.5 U 0.5 U 3.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 7/15/13 Grab GW µg/L 1.2 = 0.5 U 0.5 U 2.8 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 6/10/13 Grab GW µg/L 1.3 = 0.5 U 0.5 U 3.3 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 6/10/13 Grab GW µg/L 1.2 = 0.5 U 0.5 U 3.1 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 5/20/13 Grab GW µg/L 1.6 = 0.5 U 0.5 U 4.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 5/20/13 Grab GW µg/L 1.7 = 0.5 U 0.5 U 4.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 4/16/13 Grab GW µg/L 1.3 = 0.5 U 0.5 U 3.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 4/16/13 Grab GW µg/L 1.2 = 0.5 U 0.5 U 3.3 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐18032013 FAP‐SP‐1 3/18/13 Grab GW µg/L 1.4 = 0.5 U 0.5 U 3.7 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐18032013‐FD FAP‐SP‐1 3/18/13 Grab GW µg/L 1.4 = 0.5 U 0.5 U 3.6 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐20022013 FAP‐SP‐1 2/20/13 Grab GW µg/L 1.4 = 0.5 U 0.5 U 3.6 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐20022013‐FD FAP‐SP‐1 2/20/13 Grab GW µg/L 1.4 = 0.5 U 0.5 U 3.6 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐21012013 FAP‐SP‐1 1/21/13 Grab GW µg/L 2.0 = 0.5 U 0.6 = 5.1 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐21012013‐FD FAP‐SP‐1 1/21/13 Grab GW µg/L 1.9 = 0.5 U 0.6 = 4.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 12/19/12 Grab GW µg/L 1.8 = 0.5 U 0.6 = 4.7 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 12/19/12 Grab GW µg/L 1.7 = 0.5 U 0.5 = 4.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 11/19/12 Grab GW µg/L 2.1 = 0.5 U 0.6 = 6.1 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 11/19/12 Grab GW µg/L 2.1 = 0.5 U 0.6 = 5.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 10/18/12 Grab GW µg/L 1.7 = 0.5 U 0.5 U 5.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 10/18/12 Grab GW µg/L 1.7 = 0.5 U 0.5 = 5.1 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 9/18/12 Grab GW µg/L 0.84 J^ 0.5 U 0.21 JL 1.8 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 9/18/12 Grab GW µg/L 0.9 J^ 0.5 U 0.22 JL 2.1 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐06082012 FAP‐SP‐1 8/6/12 Grab GW µg/L 2.3 = 0.5 U 0.5 U 6.0 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐06082012FD FAP‐SP‐1 8/6/12 Grab GW µg/L 2.1 = 0.5 U 0.5 U 6.0 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐07162012 FAP‐SP‐1 7/16/12 Grab GW µg/L 1.8 = 0.5 U 0.5 U 4.6 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 2 OF 72
011369
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
D2E‐P1 (D2) D2 FAP_SP‐1‐07162012FD FAP‐SP‐1 7/16/12 Grab GW µg/L 1.9 = 0.5 U 0.5 = 4.6 = 0.5 UD2E‐P1 (D2) D2 F5Y05 FAP‐SP‐1 6/20/12 Grab GW µg/L 2.8 = 0.5 U 0.7 = 6.3 = 0.5 UD2E‐P1 (D2) D2 F5Y06 FAP‐SP‐1 6/20/12 Grab GW µg/L 2.6 = 0.5 U 0.8 = 5.9 = 0.5 UD2E‐P1 (D2) D2 F5W95 FAP‐SP‐1 5/20/12 Grab GW µg/L 1.9 = 0.5 U 0.6 = 5.0 = 0.5 UD2E‐P1 (D2) D2 F5W97 FAP‐SP‐1 5/20/12 Grab GW µg/L 1.9 = 0.5 U 0.6 = 4.9 = 0.5 UD2E‐P1 (D2) D2 F5LL6 FAP‐SP‐1 4/20/12 Grab GW µg/L 2.6 = 0.5 U 0.7 = 6.5 = 0.5 UD2E‐P1 (D2) D2 F5LL7 FAP‐SP‐1 4/20/12 Grab GW µg/L 2.7 J 0.5 U 0.75 J 6.9 J 0.5 UD2E‐P1 (D2) D2 F5HF0 FAP‐SP‐1 3/19/12 Grab GW µg/L 2.1 = 0.5 U 0.5 = 6.0 = 0.5 UD2E‐P1 (D2) D2 F5HF1 FAP‐SP‐1 3/19/12 Grab GW µg/L 2.3 = 0.5 U 0.6 = 5.9 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐27022012 FAP‐SP‐1 2/27/12 Grab GW µg/L 1.9 = 0.5 U 0.5 = 4.7 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐27022012‐FD FAP‐SP‐1 2/27/12 Grab GW µg/L 1.8 = 0.5 U 0.5 = 4.7 = 0.5 UD2E‐P1 (D2) D2 F5AJ7 FAP‐SP‐1 1/16/12 Grab GW µg/L 2.3 = 0.5 U 0.7 = 6.3 = 0.5 UD2E‐P1 (D2) D2 F5AJ8RE2 FAP‐SP‐1 1/16/12 Grab GW µg/L 2.5 J 0.5 U 0.84 J 9.2 J 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 12/19/11 Grab GW µg/L 2.3 = 0.5 U 0.6 = 5.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 12/19/11 Grab GW µg/L 2.2 = 0.5 U 0.6 = 5.4 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 11/22/11 Grab GW µg/L 2.1 = 2 U 2 U 4.9 = 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 11/22/11 Grab GW µg/L 2.3 = 2 U 2 U 5.6 = 2 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 10/17/11 Grab GW µg/L 1.6 LJ 2 U 2 U 3.8 = 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 10/17/11 Grab GW µg/L 1.6 LJ 2 U 2 U 4.0 = 2 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 10/17/11 Grab GW µg/L 2.0 = 2 U 2 U 4.6 = 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 10/17/11 Grab GW µg/L 2.0 = 2 U 2 U 4.9 = 2 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 9/19/11 Grab GW µg/L 1.8 LJ 2 U 2 U 4.0 = 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 9/19/11 Grab GW µg/L 2.1 = 2 U 2 U 3.8 = 2 UD2E‐P1 (D2) D2 F4EH0 FAP‐SP‐1 8/22/11 Grab GW µg/L 3.3 = 5 U 5 U 8.9 = 5 UD2E‐P1 (D2) D2 F4EH1 FAP‐SP‐1 8/22/11 Grab GW µg/L 3.1 = 5 U 5 U 8.9 = 5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 7/18/11 Grab GW µg/L 2.3 = 0.5 U 0.6 = 5.7 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 7/18/11 Grab GW µg/L 2.3 = 0.5 U 0.6 = 5.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 6/20/11 Grab GW µg/L 2.4 = 0.5 U 0.7 = 6.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 6/20/11 Grab GW µg/L 2.5 = 0.5 U 0.7 = 5.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 5/24/11 Grab GW µg/L 2.8 = 0.5 U 0.7 = 6.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 5/24/11 Grab GW µg/L 2.7 = 0.5 U 0.8 = 6.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 4/18/11 Grab GW µg/L 2.5 = 0.5 U 0.7 = 6.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 4/18/11 Grab GW µg/L 2.4 = 0.5 U 0.7 = 6.0 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐24032011‐DUP FAP‐SP‐1 3/24/11 GRAB GW µg/L 2.6 = 0.5 U 0.8 = 6.1 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐24032011 FAP‐SP‐1 3/24/11 GRAB GW µg/L 2.7 = 0.5 U 0.8 = 6.2 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1_Q111_DUP FAP‐SP‐1 2/14/11 GRAB GW µg/L 2.2 J 0.5 UJ 0.6 J 6.1 J 0.5 UJD2E‐P1 (D2) D2 FAP_SP‐1_Q111 FAP‐SP‐1 2/14/11 GRAB GW µg/L 2.2 J 0.5 UJ 0.7 J 6.1 J 0.5 UJD2E‐P1 (D2) D2 FAP_SP‐1_110125‐DUP FAP‐SP‐1 1/25/11 GRAB GW µg/L 2.2 = 0.5 U 0.6 = 5.4 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1_110125 FAP‐SP‐1 1/25/11 GRAB GW µg/L 2.2 = 0.5 U 0.7 = 5.6 = 0.5 UD2E‐P1 (D2) D2 F3RM3 FAP‐SP‐1 12/14/10 GRAB GW µg/L 2.4 = 0.5 U 0.69 = 5.9 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 3 OF 72
011370
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
D2E‐P1 (D2) D2 F3RM2 FAP‐SP‐1 12/14/10 GRAB GW µg/L 2.3 = 0.5 U 0.66 = 5.7 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1 DUP FAP‐SP‐1 9/23/10 GRAB GW µg/L 1.5 = 0.5 U 0.5 U 4.2 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1 FAP‐SP‐1 9/23/10 GRAB GW µg/L 1.6 = 0.5 U 0.5 U 4.4 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐Q310‐DUP FAP‐SP‐1 9/7/10 GRAB GW µg/L 1.9 = 0.5 U 0.6 = 5.0 = 0.5 UD2E‐P1 (D2) D2 FAP_SP‐1‐Q310 FAP‐SP‐1 9/7/10 GRAB GW µg/L 2.1 = 0.5 U 0.6 = 5.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 6/22/10 Grab GW µg/L 1.9 = 0.5 U 0.6 = 5.3 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 6/22/10 Grab GW µg/L 2.0 = 0.5 U 0.6 = 5.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 3/18/10 Grab GW µg/L 1.8 = 0.5 U 0.6 = 5.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP FAP‐SP‐1 3/18/10 Grab GW µg/L 1.8 = 0.5 U 0.6 = 5.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q110 FAP‐SP‐1 2/1/10 Grab GW µg/L 2.0 = 0.5 U 0.6 = 5.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q110 FAP‐SP‐1 2/1/10 Grab GW µg/L 2.2 = 0.5 U 0.6 = 5.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 FAP‐SP‐1 11/30/09 Grab GW µg/L 1.8 = 0.5 U 0.5 U 4.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q409 FAP‐SP‐1 10/28/09 Grab GW µg/L 1.8 = 0.5 U 0.5 = 4.8 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q409 FAP‐SP‐1 10/28/09 Grab GW µg/L 2.0 = 0.5 U 0.5 = 5.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q309 FAP‐SP‐1 7/6/09 Grab GW µg/L 2.5 = 0.5 U 0.9 = 7.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q309 FAP‐SP‐1 7/6/09 Grab GW µg/L 2.6 = 0.5 U 0.9 = 8.1 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q209 FAP‐SP‐1 4/20/09 Grab GW µg/L 3.0 = 0.5 U 1.0 = 7.7 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q209 FAP‐SP‐1 4/20/09 Grab GW µg/L 3.1 = 0.5 U 1.0 = 8.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 090212 FAP‐SP‐1 2/12/09 Grab GW µg/L 3.2 = 0.5 U 1.1 = 7.3 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 090212‐DUP FAP‐SP‐1 2/12/09 Grab GW µg/L 3.1 = 0.5 U 1.0 = 7.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 081111 FAP‐SP‐1 11/11/08 Grab GW µg/L 3.0 = 0.5 U 1.0 = 7.8 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 081111‐DUP FAP‐SP‐1 11/11/08 Grab GW µg/L 3.0 = 0.5 U 0.9 = 7.5 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080707 FAP‐SP‐1 7/7/08 Grab GW µg/L 3.4 = 0.5 U 1.2 = 8.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080414 FAP‐SP‐1 4/14/08 Grab GW µg/L 4.6 = 0.5 U 1.5 = 11.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080414‐DUP FAP‐SP‐1 4/14/08 Grab GW µg/L 4.6 = 0.5 U 1.5 = 12.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080218 FAP‐SP‐1 2/18/08 Grab GW µg/L 3.8 = 0.5 U 1.4 = 9.7 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080218‐DUP FAP‐SP‐1 2/18/08 Grab GW µg/L 3.7 = 0.5 U 1.2 = 9.4 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 071029 FAP‐SP‐1 10/28/07 Grab GW µg/L 4.4 = 0.5 U 1.5 = 11.4 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 071029‐DUP FAP‐SP‐1 10/28/07 Grab GW µg/L 4.4 = 0.5 U 1.6 = 11.1 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 070823 FAP‐SP‐1 8/23/07 Grab GW µg/L 4.1 = 0.5 U 1.5 = 10.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 070602 FAP‐SP‐1 6/2/07 Grab GW µg/L 4.1 = 0.5 U 1.5 = 10.2 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 070602‐DUP FAP‐SP‐1 6/2/07 Grab GW µg/L 4.2 = 0.5 U 1.3 = 9.9 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 B07 FAP‐SP‐1 2/20/07 Grab GW µg/L 4.2 = 0.5 U 1.5 = 12.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 B07 Dup FAP‐SP‐1 2/20/07 Grab GW µg/L 4.3 = 0.5 U 1.5 = 12.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 C07 FAP‐SP‐1 2/20/07 Grab GW µg/L 4.1 = 0.5 U 1.4 = 12.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 C07 Dup FAP‐SP‐1 2/20/07 Grab GW µg/L 4.2 = 0.5 U 1.5 = 12.3 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐107 FAP‐SP‐1 2/19/07 Grab GW µg/L 4.2 = 0.5 U 1.6 = 12.1 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 061016 FAP‐SP‐1 10/16/06 Grab GW µg/L 4.6 = 0.5 U 1.7 = 11.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 0600816 FAP‐SP‐1 8/16/06 Grab GW µg/L 5.6 = 0.5 U 1.9 = 13.6 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 0600719 FAP‐SP‐1 7/19/06 Grab GW µg/L 5.6 = 0.5 U 2.1 = 13.4 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 4 OF 72
011371
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
D2E‐P1 (D2) D2 FAP SP‐1 060524 FAP‐SP‐1 5/24/06 Grab GW µg/L 4.7 = 0.5 U 1.9 = 12.8 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060329 FAP‐SP‐1 3/29/06 Grab GW µg/L 5.0 = 0.5 U 1.0 = 12.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060308 FAP‐SP‐1 3/8/06 Grab GW µg/L 4.3 = 0.5 U 1.5 = 13.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060127 FAP‐SP‐1 1/27/06 Grab GW µg/L 4.6 = 0.5 U 2.3 = 12.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060109 FAP‐SP‐1 1/9/06 Grab GW µg/L 6.0 = 0.5 U 2.5 = 13.0 = 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 051130 FAP‐SP‐1 11/30/05 Grab GW µg/L 5.0 = 0.5 U 1.4 = 11.0 = 0.5 UD2E‐P1 (D2) D2 FAP Infl 102505 FAP‐SP‐1 10/25/05 Grab GW µg/L 6.6 = 0.5 U 2.7 = 14.0 = 0.5 UD2E‐P1 (D2) D2 FAP DUP 102505 FAP‐SP‐1 10/25/05 Grab GW µg/L 6.4 = 0.5 U 2.7 = 14.0 = 0.5 UD2E‐P1 (D2) D2 FAP Infl 102105 FAP‐SP‐1 10/21/05 Grab GW µg/L 5.3 = 0.5 U 2.2 = 12.0 = 0.5 UD2E‐P1 (D2) D2 FAP Infl 101905 FAP‐SP‐1 10/19/05 Grab GW µg/L 5.7 = 0.5 U 2.1 = 12.0 = 0.5 UD2E‐P1 (D2) D2 ASTP INFLUENT FAP‐SP‐1 3/17/05 Grab GW µg/L 6.0 = 0.5 U 2.4 = 15.0 = 0.5 UD2E‐P1 (D2) D2 ASTP INFLUENT FAP‐SP‐1 2/22/05 Grab GW µg/L 5.6 = 0.5 U 2.4 = 14.0 = 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT1 FAP‐SP‐1 1/5/05 Grab GW µg/L 5.7 = 0.5 U 2.5 = 13.0 = 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT2 FAP‐SP‐1 1/5/05 Grab GW µg/L 5.3 = 0.5 U 2.4 = 12.0 = 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT3 FAP‐SP‐1 1/5/05 Grab GW µg/L 4.9 = 0.5 U 2.3 = 13.0 = 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT4 FAP‐SP‐1 1/5/05 Grab GW µg/L 5.4 = 0.5 U 2.4 = 12.0 = 0.5 U
DM‐01 (S) NA 5/10/2020 0:00 unknownDM‐01 (S) S FX085 NA 5/2/2000 0:00 BAIL GW µg/L 2 = 0.8 LJ 2 = 3 = 1 UDM‐01 (S) S FGG07 NA 8/3/1999 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 UDM‐01 (S) S FQ881 NA 11/12/1997 0:00 unknown GW µg/L 3 = 2 = 2 = 6 = 1 UDM‐01 (S) S FW896 NA 12/12/1996 0:00 unknown GW µg/L 2 = 1 = 2 = 7 = 1 UDM‐01 (S) S 930949‐3 NA 9/28/1993 0:00 unknown GW µg/L 4.9 = 1.8 = 3 = 4.5 = <0.2DM‐01 (S) S 930933‐1 NA 9/22/1993 0:00 unknown GW µg/L 3.6 = 1.6 = 2.9 = 3.6 = <0.2
DM‐02 (I) NA 5/10/2020 0:00 unknownDM‐02 (I) I FGG55 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 6 = 2 U 2 = 29 = 2 UDM‐02 (I) I FGG08 NA 8/3/1999 0:00 unknown GW µg/L 9 = 1 U 3 = 54 = 1 UDM‐02 (I) I FQ894 NA 11/17/1997 0:00 unknown GW µg/L 8 = 1 U 3 = 47 = 1 UDM‐02 (I) I FW889 NA 12/11/1996 0:00 unknown GW µg/L 8 = 1 U 3 = 42 D NDDM‐02 (I) I 931057‐3 NA 10/28/1993 0:00 unknown GW µg/L 5.9 = <0.2 3.5 = 43 = <0.2DM‐02 (I) I 930949‐2 NA 9/28/1993 0:00 unknown GW µg/L 6.9 = <0.2 3.5 = 43 = <0.2
DM‐03 (I) NA 5/10/2020 0:00 unknownDM‐03 (I) I FGS96 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 4 = 1 U 2 = 11 = 1 UDM‐03 (I) I FGF96 NA 8/3/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 18 = 1 UDM‐03 (I) I FQ893 NA 11/17/1997 0:00 unknown GW µg/L 5 = 1 U 2 = 20 = 1 UDM‐03 (I) I FW890 NA 12/11/1996 0:00 unknown GW µg/L 5 = 1 U 2 = 24 = NDDM‐03 (I) I 930949‐1 NA 9/28/1993 0:00 unknown GW µg/L 5.8 = <0.2 3.2 = 31 = <0.2DM‐03 (I) I 930949‐5 NA 9/28/1993 0:00 unknown GW µg/L 6.3 = <0.2 3.5 = 32 = <0.2
DM‐04 (S) NA 5/10/2020 0:00 unknownDM‐04 (S) S FX089 NA 5/2/2000 0:00 BAIL GW µg/L 1 = 1 = 0.8 LJ 0.6 LJ 1 UDM‐04 (S) S FGF97 NA 8/3/1999 0:00 unknown GW µg/L 0.9 LJ 0.8 LJ 1 = 0.7 LJ 1 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 5 OF 72
011372
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
DM‐04 (S) S FQ877 NA 11/12/1997 0:00 unknown GW µg/L 0.9 J 15 = 0.8 J 0.9 J 1 UDM‐04 (S) S FW892 NA 12/11/1996 0:00 unknown GW µg/L 2 = 0.6 J 2 = 0.8 J 1 UDM‐04 (S) S 930949‐4 NA 9/29/1993 0:00 unknown GW µg/L 1.5 = 5.6 = 2 = 1.1 = <0.2
DM‐05 (S) NA 5/10/2020 0:00 unknownDM‐05 (S) S DM‐05‐S‐8‐022014 DM‐O5‐S‐8 2/18/2014 8:18 PDB GW µg/L 0.5 U 0.7 = 0.5 U 0.5 U 0.5 UDM‐05 (S) S F6PA0 DM‐O5‐S‐8 2/12/2013 0:00 PDB GW µg/L 0.25 LJ 1.1 = 0.5 U 0.32 LJ 0.5 UDM‐05 (S) S F5G69 DM‐05‐S‐8 2/28/2012 8:35 PDB GW µg/L 0.33 LJ 0.5 U 0.1 LJ 0.36 LJ 0.5 UDM‐05 (S) S DM‐05‐S‐8‐Q111 DM‐05‐S‐8 2/16/2011 8:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐05 (S) S F3LR9 DM‐05‐S‐8‐Q310‐FD 9/3/2010 9:10 PDB GW µg/L 0.47 LJ 0.5 U 0.5 U 0.52 = 0.5 UDM‐05 (S) S F3LR8 DM‐05‐S‐8‐Q310 9/3/2010 9:05 PDB GW µg/L 0.55 = 0.5 U 0.5 U 0.58 = 0.5 UDM‐05 (S) S F3LR7 DM‐05‐S‐5‐Q310 9/3/2010 9:00 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 0.51 = 0.5 UDM‐05 (S) S F3LR6 DM‐05‐S‐2‐Q310 9/3/2010 8:55 PDB GW µg/L 0.5 U 3.5 = 0.5 U 1.2 = 0.5 UDM‐05 (S) S DM‐05‐S‐8_100201‐FD DM‐05‐S‐8 2/1/2010 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐05 (S) S DM‐05‐S‐8_100201 DM‐05‐S‐8 2/1/2010 10:32 PDB GW µg/L 0.5 = 0.5 U 0.5 U 0.5 U 0.5 UDM‐05 (S) S F3B47 DM‐05‐S‐8 10/26/2009 8:45 PDB GW µg/L 0.54 = 0.5 U 0.32 LJ 0.48 LJ 0.5 UDM‐05 (S) S F3B45 DM‐05‐S‐5 10/26/2009 8:41 PDB GW µg/L 0.43 LJ 0.5 U 0.28 LJ 0.44 LJ 0.5 UDM‐05 (S) S F3B44 DM‐05‐S‐2 10/26/2009 8:38 PDB GW µg/L 0.5 U 1.5 = 0.5 U 0.51 = 0.5 UDM‐05 (S) S FW573 NA 2/1/2000 0:00 unknown GW µg/L 0.9 LJ 4 = 0.9 LJ 1 = 1 UDM‐05 (S) S FGR75 NA 11/3/1999 0:00 unknown GW µg/L 0.6 LJ 2 = 3 = 1 = 1 UDM‐05 (S) S FQ813 NA 11/18/1997 0:00 unknown GW µg/L 2 = 10 = 1 = 3 = 1 UDM‐05 (S) S 930948‐1 NA 9/29/1993 0:00 unknown GW µg/L 2.2 = 4.3 = 2 = 2.4 = <0.2
DM‐06 (I1/I2) NA 5/10/2020 0:00 unknownDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐2‐022014 DM‐06‐I1/I2‐2 2/18/2014 8:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.9 = 0.5 UDM‐06 (I1/I2) I1/I2 F6PA2 DM‐06‐I1/I2‐2‐FD 2/12/2013 0:00 PDB GW µg/L 0.49 LJ 0.5 U 0.16 LJ 0.99 = 0.5 UDM‐06 (I1/I2) I1/I2 F6PA1 DM‐06‐I1/I2‐2 2/12/2013 0:00 PDB GW µg/L 0.54 = 0.5 U 0.18 LJ 1.2 = 0.5 UDM‐06 (I1/I2) I1/I2 F5G70 DM‐06‐I1/I2‐2 2/27/2012 9:38 PDB GW µg/L 0.51 = 0.5 U 0.2 LJ 1.1 = 0.5 UDM‐06 (I1/I2) I1/I2 F3S31 DM‐06‐I1/I2‐2 2/15/2011 8:02 PDB GW µg/L 0.98 = 0.5 U 0.56 = 3.7 J 0.5 UDM‐06 (I1/I2) I1/I2 F3LS6 DM‐06‐I1/I2‐27‐Q310 9/3/2010 11:55 PDB GW µg/L 0.77 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS5 DM‐06‐I1/I2‐22‐Q310 9/3/2010 11:50 PDB GW µg/L 0.78 = 0.5 U 0.5 U 1.9 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS4 DM‐06‐I1/I2‐17‐Q310‐FD 9/3/2010 11:40 PDB GW µg/L 0.73 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS3 DM‐06‐I1/I2‐17‐Q310 9/3/2010 11:35 PDB GW µg/L 0.75 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS2 DM‐06‐I1/I2‐12‐Q310 9/3/2010 11:30 PDB GW µg/L 0.72 = 0.5 U 0.35 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS1 DM‐06‐I1/I2‐7‐Q310 9/3/2010 11:25 PDB GW µg/L 0.7 = 0.5 U 0.32 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS0 DM‐06‐I1/I2‐2‐Q310 9/3/2010 11:20 PDB GW µg/L 0.7 = 0.5 U 0.35 LJ 2.1 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐17_100202‐FD DM‐06‐I1/I2‐17 2/2/2010 9:01 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐27_100202 DM‐06‐I1/I2‐27 2/2/2010 8:07 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐22_100202 DM‐06‐I1/I2‐22 2/2/2010 8:05 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐17_100202 DM‐06‐I1/I2‐17 2/2/2010 8:01 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐12_100202 DM‐06‐I1/I2‐12 2/2/2010 7:59 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐7_100202 DM‐06‐I1/I2‐7 2/2/2010 7:57 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2.1 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 6 OF 72
011373
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
DM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐2_100202 DM‐06‐I1/I2‐2 2/2/2010 7:55 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.9 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B53 DM‐06‐I1/I2‐27 10/28/2009 8:20 PDB GW µg/L 0.71 = 0.5 U 0.32 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B52 DM‐06‐I1/I2‐22 10/28/2009 8:16 PDB GW µg/L 0.69 = 0.5 U 0.33 LJ 1.7 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B51 DM‐06‐I1/I2‐17 10/28/2009 8:12 PDB GW µg/L 0.71 = 0.5 U 0.33 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B50 DM‐06‐I1/I2‐12 10/28/2009 8:08 PDB GW µg/L 0.73 = 0.5 U 0.34 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B49 DM‐06‐I1/I2‐7 10/28/2009 8:04 PDB GW µg/L 0.7 = 0.5 U 0.33 LJ 1.7 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B48 DM‐06‐I1/I2‐2 10/28/2009 8:00 PDB GW µg/L 0.68 = 0.5 U 0.32 LJ 1.7 = 0.5 UDM‐06 (I1/I2) I FW589 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 2 = 1 U 1 = 6 = 1 UDM‐06 (I1/I2) I FW552 NA 2/8/2000 0:00 unknown GW µg/L 2 = 1 U 1 = 5 = 1 UDM‐06 (I1/I2) I FGR60 NA 11/1/1999 0:00 unknown GW µg/L 3 = 1 U 4 = 4 = 1 UDM‐06 (I1/I2) I FGF78 NA 7/30/1999 0:00 unknown GW µg/L 2 = 1 U 2 = 7 = 1 UDM‐06 (I1/I2) I FQ858 NA 11/5/1997 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 UDM‐06 (I1/I2) I FQ859 NA 11/5/1997 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 UDM‐06 (I1/I2) I FW503 NA 12/17/1996 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 UDM‐06 (I1/I2) I 931003‐2 NA 10/2/1993 0:00 unknown GW µg/L 2.9 = <0.2 2.1 = 6.8 = NDDM‐06 (I1/I2) I 931003‐1 NA 10/2/1993 0:00 unknown GW µg/L 3 = <0.2 2.3 = 7.2 = ND
DM‐07 (I1/I2) NA 5/10/2020 0:00 unknownDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐27‐022014 DM‐07‐I1/I2‐27 2/17/2014 13:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐12‐022014 DM‐07‐I1/I2‐12 2/17/2014 13:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F6PA3 DM‐07‐I1/I2‐12 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F6PA4 DM‐07‐I1/I2‐27 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F6CA1 DM‐07‐I1/I2‐27 8/20/2012 8:35 PDB GW µg/L 0.5 U 0.055 LJ 0.5 U 0.059 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F6CA0 DM‐07‐I1/I2‐12 8/20/2012 8:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.085 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F5G75 DM‐07‐I1/I2‐27 2/28/2012 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G74 DM‐07‐I1/I2‐22 2/28/2012 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G72 DM‐07‐I1/I2‐17 2/28/2012 10:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G71 DM‐07‐I1/I2‐12 2/28/2012 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G76 DM‐07‐I1/I2‐7 2/28/2012 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G73 DM‐07‐I1/I2‐2 2/28/2012 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F4EA2 DM‐07‐I1/I2‐12‐Q311 8/22/2011 9:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UDM‐07 (I1/I2) I1/I2 F4EA1 DM‐07‐I1/I2‐7‐Q311 8/22/2011 9:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UDM‐07 (I1/I2) I1/I2 F4EA0 DM‐07‐I1/I2‐2‐Q311 8/22/2011 9:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UDM‐07 (I1/I2) I1/I2 F3S35 DM‐07‐I1/I2‐12 2/15/2011 8:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐07 (I1/I2) I1/I2 F3S34 DM‐07‐I1/I2‐7 2/15/2011 8:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐07 (I1/I2) I1/I2 F3S33 DM‐07‐I1/I2‐2 2/15/2011 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐07 (I1/I2) I1/I2 F3S32 DM‐07‐I1/I2‐2 2/15/2011 8:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.72 J 0.5 UDM‐07 (I1/I2) I1/I2 F3LT2 DM‐07‐I1/I2‐27‐Q310 9/3/2010 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.37 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LT1 DM‐07‐I1/I2‐22‐Q310 9/3/2010 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LT0 DM‐07‐I1/I2‐17‐Q310 9/3/2010 10:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LS9 DM‐07‐I1/I2‐12‐Q310 9/3/2010 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.37 LJ 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 7 OF 72
011374
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
DM‐07 (I1/I2) I1/I2 F3LS8 DM‐07‐I1/I2‐7‐Q310 9/3/2010 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.34 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LS7 DM‐07‐I1/I2‐2‐Q310 9/3/2010 10:20 PDB GW µg/L 0.19 LJ 0.5 U 0.5 U 0.32 LJ 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐27_100202 DM‐07‐I1/I2‐27 2/2/2010 8:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐22_100202 DM‐07‐I1/I2‐22 2/2/2010 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐17_100202 DM‐07‐I1/I2‐17 2/2/2010 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐12_100202 DM‐07‐I1/I2‐12 2/2/2010 8:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐7_100202 DM‐07‐I1/I2‐7 2/2/2010 8:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐2_100202 DM‐07‐I1/I2‐2 2/2/2010 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F3B32 DM‐07‐I1/I2‐27 10/26/2009 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B31 DM‐07‐I1/I2‐22 10/26/2009 10:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B30 DM‐07‐I1/I2‐17 10/26/2009 9:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.3 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B29 DM‐07‐I1/I2‐12 10/26/2009 9:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.27 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B28 DM‐07‐I1/I2‐7 10/26/2009 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.3 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B27 DM‐07‐I1/I2‐2 10/26/2009 9:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐07 (I1/I2) I FGS95 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 1 = 1 U 1 U 1 = 1 UDM‐07 (I1/I2) I FGF76 NA 7/30/1999 0:00 unknown GW µg/L 1 = 1 U 1 U 1 = 1 UDM‐07 (I1/I2) I FQ847 NA 11/3/1997 0:00 unknown GW µg/L 1 = 1 U 1 U 1 = 1 UDM‐07 (I1/I2) I FW876 NA 12/9/1996 0:00 unknown GW µg/L 2 = 1 U 0.6 J 2 = NDDM‐07 (I1/I2) I 931013‐1 NA 10/7/1993 0:00 unknown GW µg/L 2.7 = <0.2 0.8 = 1.3 = <0.2DM‐07 (I1/I2) I 931001‐1 NA 10/1/1993 0:00 unknown GW µg/L 1.7 = <0.2 0.4 = 0.7 = <0.2
DM‐08 (I1/I2) NA 5/10/2020 0:00 unknownDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22‐022014 DM‐08‐I1/I2‐22 2/18/2014 10:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12‐022014 DM‐08‐I1/I2‐12 2/18/2014 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F6PA6 DM‐08‐I1/I2‐22 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.16 LJ 0.5 U 0.26 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F6PA5 DM‐08‐I1/I2‐12 2/12/2013 0:00 PDB GW µg/L 0.14 LJ 0.22 LJ 0.5 U 0.27 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F5G79 DM‐08‐I1/I2‐22‐FD 2/27/2012 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F5G78 DM‐08‐I1/I2‐22 2/27/2012 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F5G77 DM‐08‐I1/I2‐12 2/27/2012 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F3S37 DM‐08‐I1/I2‐22 2/15/2011 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐08 (I1/I2) I1/I2 F3S36 DM‐08‐I1/I2‐12 2/15/2011 8:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22_100201 DM‐08‐I1/I2‐22 2/1/2010 14:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12_100201 DM‐08‐I1/I2‐12 2/1/2010 14:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22‐Q209 DM‐08‐I1/I2‐22 4/20/2009 10:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12‐Q209 DM‐08‐I1/I2‐12 4/20/2009 10:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F2913 DM‐08‐I1/I2‐2 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2916 DM‐08‐I1/I2‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2915 DM‐08‐I1/I2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2917 DM‐08‐I1/I2‐27 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.31 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2918 DM‐08‐I1/I2‐17 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.35 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2919 DM‐08‐I1/I2‐22 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.36 LJ 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 8 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
DM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22‐Q407 DM‐08‐I1/I2‐22 10/2/2007 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12‐Q407 DM‐08‐I1/I2‐12 10/2/2007 8:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1NR4 DM‐08‐I‐27 7/12/2005 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1NR3 DM‐08‐I‐22 7/12/2005 8:54 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.44 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1NR2 DM‐08‐I‐17 7/12/2005 8:50 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1NR0 DM‐08‐I‐12 7/12/2005 8:46 PDB GW µg/L 0.26 LJ 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1NQ9 DM‐08‐I‐7 7/12/2005 8:42 PDB GW µg/L 0.26 LJ 0.5 U 0.5 U 0.38 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1NQ8 DM‐08‐I‐2 7/12/2005 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1DL7 DM‐08‐I‐27 4/18/2005 10:07 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 0.32 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL6 DM‐08‐I‐22 4/18/2005 10:06 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL5 DM‐08‐I‐17 4/18/2005 10:05 PDB GW µg/L 0.3 LJ 0.5 U 0.5 U 0.35 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL3 DM‐08‐I‐12 4/18/2005 10:03 PDB GW µg/L 0.32 LJ 0.5 U 0.1 LJ 0.35 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL2 DM‐08‐I‐7 4/18/2005 10:02 PDB GW µg/L 0.18 LJ 0.5 U 0.5 U 0.21 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL1 DM‐08‐I‐2 4/18/2005 10:00 PDB GW µg/L 0.24 LJ 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17G2 DM‐08‐I‐27 11/10/2004 10:15 PDB GW µg/L 0.34 LJ 0.5 U 0.5 U 0.46 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17G1 DM‐08‐I‐22 11/10/2004 10:13 PDB GW µg/L 0.37 LJ 0.5 U 0.5 U 0.44 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17G0 DM‐08‐I‐17 11/10/2004 10:11 PDB GW µg/L 0.33 LJ 0.5 U 0.5 U 0.38 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17F8 DM‐08‐I‐12 11/10/2004 10:07 PDB GW µg/L 0.35 LJ 0.5 U 0.5 U 0.41 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17F7 DM‐08‐I‐7 11/10/2004 10:05 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17F6 DM‐08‐I‐2 11/10/2004 10:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐08 (I1/I2) I1/I2 DM08‐020221 NA 2/21/2002 15:15 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UDM‐08 (I1/I2) I FW583 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 0.7 LJ 1 U 1 U 1 = 1 UDM‐08 (I1/I2) I FW549 NA 2/8/2000 0:00 unknown GW µg/L 0.8 LJ 1 U 1 U 3 = 1 UDM‐08 (I1/I2) I FGR59 NA 11/1/1999 0:00 unknown GW µg/L 0.8 LJ 1 U 0.5 LJ 1 = 1 UDM‐08 (I1/I2) I FGF86 NA 8/2/1999 0:00 unknown GW µg/L 0.5 LJ 1 U 1 U 2 = 1 UDM‐08 (I1/I2) I FQ854 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 0.7 J 1 UDM‐08 (I1/I2) I FW878 NA 12/9/1996 0:00 unknown GW µg/L 1 U 1 U 1 U 0.5 J NDDM‐08 (I1/I2) I 931019‐1 NA 10/8/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
DM‐09 (S) NA 5/10/2020 0:00 unknownDM‐09 (S) S DM‐09‐S‐7‐022014 DM‐09‐S‐7 2/18/2014 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S F6PA7 DM‐09‐S‐7 2/12/2013 0:00 PDB GW µg/L 0.47 LJ 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S F5G80 DM‐09‐S‐7 2/27/2012 9:19 PDB GW µg/L 0.45 LJ 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐09 (S) S F3S38 DM‐09‐S‐7 2/15/2011 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐09 (S) S DM‐09‐S‐7_100201 DM‐09‐S‐7 2/1/2010 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM‐09‐S‐7‐Q209 DM‐09‐S‐7 4/20/2009 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM‐09‐S‐7‐Q408 DM‐09‐S‐7 10/6/2008 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM‐09‐S‐7‐Q407 DM‐09‐S‐7 10/2/2007 10:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 = 0.5 UDM‐09 (S) S F2641 DM‐09‐S‐7 8/28/2006 13:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S F1NR7 DM‐09‐S‐12 7/12/2005 8:30 PDB GW µg/L 0.49 LJ 0.15 LJ 0.25 LJ 0.93 = 0.5 UDM‐09 (S) S F1NR6 DM‐09‐S‐7 7/12/2005 8:28 PDB GW µg/L 0.5 = 0.16 LJ 0.28 LJ 0.93 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 9 OF 72
011376
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
DM‐09 (S) S F1DL8 DM‐09‐S‐2 4/18/2005 9:38 PDB GW µg/L 3.1 UJv 3.1 U 3.1 UJv 3.1 U 3.1 UDM‐09 (S) S F1DL9 DM‐09‐S‐7 4/18/2005 9:36 PDB GW µg/L 0.28 LJv 0.5 U 0.12 LJv 0.4 LJ 0.5 UDM‐09 (S) S F1DM0 DM‐09‐S‐12 4/18/2005 9:34 PDB GW µg/L 0.25 LJv 0.5 U 0.12 LJv 0.38 LJ 0.5 UDM‐09 (S) S F17G5 DM‐09‐S‐12 11/10/2004 9:56 PDB GW µg/L 0.47 LJ 0.5 U 0.5 U 0.55 J 0.5 UDM‐09 (S) S F17G4 DM‐09‐S‐7 11/10/2004 9:54 PDB GW µg/L 0.42 LJv 0.5 U 0.5 UJv 0.53 J 0.5 UDM‐09 (S) S F17G3 DM‐09‐S‐2 11/10/2004 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM09‐020221 NA 2/21/2002 16:30 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐09 (S) S FX081 NA 5/2/2000 0:00 BAIL GW µg/L 2 U 2 U 2 U 2 U 2 UDM‐09 (S) S FGF85 NA 8/2/1999 0:00 unknown GW µg/L 0.5 LJ 1 U 1 U 1 = 1 UDM‐09 (S) S FQ856 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UDM‐09 (S) S FQ855 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 0.9 J 1 UDM‐09 (S) S 931019‐2 NA 10/8/1993 0:00 unknown GW µg/L 0.3 = <0.2 <0.2 0.4 = <0.2
DM‐10 (S) NA 5/10/2020 0:00 unknownDM‐10 (S) S FGF68 NA 7/29/1999 0:00 unknown GW µg/L 1 = 1 U 1 U 2 = 1 UDM‐10 (S) S FQ846 NA 11/3/1997 0:00 unknown GW µg/L 1 = 1 U 1 U 2 = 1 UDM‐10 (S) S FW877 NA 12/9/1996 0:00 unknown GW µg/L 2 = 1 U 0.5 J 2 = NDDM‐10 (S) S 931013‐2 NA 10/7/1993 0:00 unknown GW µg/L 0.6 = <0.2 <0.2 0.9 = <0.2
DM‐11 (S) NA 5/10/2020 0:00 unknownDM‐11 (S) S FGF45 NA 7/27/1999 0:00 unknown GW µg/L 0.9 J 1 U 1 = 1 U 1 UDM‐11 (S) S FQ866 NA 11/6/1997 0:00 unknown GW µg/L 1 = 1 U 1 = 1 U 1 UDM‐11 (S) S FW507 NA 12/17/1996 0:00 unknown GW µg/L 1 = 1 U 1 = 1 U 1 UDM‐11 (S) S 931057‐2 NA 10/28/1993 0:00 unknown GW µg/L 2.1 = <0.2 2.5 = 0.9 = <0.2DM‐11 (S) S 931019‐3 NA 10/8/1993 0:00 unknown GW µg/L 2.4 = <0.2 1.8 = 0.6 = <0.2
DM‐12 (I1) NA 5/10/2020 0:00 unknownDM‐12 (I1) I1 F6PA8 DM‐12‐I1‐22 2/19/2013 0:00 PDB GW µg/L 2 = 0.5 U 0.39 LJ 2.6 = 0.5 UDM‐12 (I1) I1 F5G81 DM‐12‐I1‐22 2/27/2012 13:00 PDB GW µg/L 2 = 0.5 U 0.5 U 2.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐22‐Q111 DM‐12‐I1‐22 2/14/2011 12:40 PDB GW µg/L 1.8 = 0.5 U 0.5 U 2.8 = 0.5 UDM‐12 (I1) I1 F3LT7 DM‐12‐I1‐7‐Q310 9/3/2010 10:00 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3LT9 DM‐12‐I1‐27‐Q310 9/3/2010 9:55 PDB GW µg/L 2 = 0.5 U 0.39 LJ 3.2 = 0.5 UDM‐12 (I1) I1 F3LT8 DM‐12‐I1‐22‐Q310 9/3/2010 9:50 PDB GW µg/L 1.9 = 0.5 U 0.33 LJ 3.3 = 0.5 UDM‐12 (I1) I1 F3LT6 DM‐12‐I1‐17‐Q310 9/3/2010 9:45 PDB GW µg/L 1.9 = 0.5 U 0.34 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3LT5 DM‐12‐I1‐12‐Q310 9/3/2010 9:40 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 3.2 = 0.5 UDM‐12 (I1) I1 F3LT4 DM‐12‐I1‐2‐Q310‐FD 9/3/2010 9:35 PDB GW µg/L 2 = 0.5 U 0.37 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3LT3 DM‐12‐I1‐2‐Q310 9/3/2010 9:30 PDB GW µg/L 2.1 = 0.5 U 0.43 LJ 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐2_100201‐FD DM‐12‐I1‐2 2/1/2010 9:23 PDB GW µg/L 2.2 = 0.5 U 0.5 U 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐2_100201 DM‐12‐I1‐2 2/1/2010 8:23 PDB GW µg/L 2.2 = 0.5 U 0.5 U 3.5 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐7_100201 DM‐12‐I1‐7 2/1/2010 8:20 PDB GW µg/L 1.9 = 0.5 U 0.5 U 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐12_100201 DM‐12‐I1‐12 2/1/2010 8:18 PDB GW µg/L 2.1 = 0.5 U 0.5 U 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐17_100201 DM‐12‐I1‐17 2/1/2010 8:16 PDB GW µg/L 2.3 = 0.5 U 0.5 U 3.7 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐22_100201 DM‐12‐I1‐22 2/1/2010 8:14 PDB GW µg/L 2.1 = 0.5 U 0.5 U 3.8 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 10 OF 72
011377
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
DM‐12 (I1) I1 DM‐12‐I1‐27_100201 DM‐12‐I1‐27 2/1/2010 8:10 PDB GW µg/L 2.1 = 0.5 U 0.5 U 3.7 = 0.5 UDM‐12 (I1) I1 F3B60 DM‐12‐I1‐27 10/26/2009 11:37 PDB GW µg/L 2.5 = 0.5 U 0.43 LJ 3.4 = 0.5 UDM‐12 (I1) I1 F3B59 DM‐12‐I1‐22 10/26/2009 11:34 PDB GW µg/L 2.4 = 0.5 U 0.43 LJ 3.4 = 0.5 UDM‐12 (I1) I1 F3B58 DM‐12‐I1‐17 10/26/2009 11:31 PDB GW µg/L 2.3 = 0.5 U 0.43 LJ 3.2 = 0.5 UDM‐12 (I1) I1 F3B57 DM‐12‐I1‐12 10/26/2009 11:28 PDB GW µg/L 2.4 = 0.5 U 0.49 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3B56 DM‐12‐I1‐7 10/26/2009 11:23 PDB GW µg/L 2.4 = 0.5 U 0.46 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3B55 DM‐12‐I1‐2 10/26/2009 11:20 PDB GW µg/L 2.5 = 0.5 U 0.47 LJ 3.2 = 0.5 UDM‐12 (I1) I FGS97 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 11 = 2 U 4 = 42 = 2 UDM‐12 (I1) I FW577 NA 2/1/2000 0:00 unknown GW µg/L 7 = 1 U 4 = 15 = 1 UDM‐12 (I1) I FW578 NA 2/1/2000 0:00 unknown GW µg/L 7 = 1 U 4 = 15 = 1 UDM‐12 (I1) I FGR80 NA 11/4/1999 0:00 unknown GW µg/L 13 = 1 U 11 = 33 = 1 UDM‐12 (I1) I FGF44 NA 7/27/1999 0:00 unknown GW µg/L 13 = 1 U 6 = 53 = 1 UDM‐12 (I1) I FGF43 NA 7/27/1999 0:00 unknown GW µg/L 13 = 1 U 6 = 54 = 1 UDM‐12 (I1) I FQ892 NA 11/13/1997 0:00 unknown GW µg/L 16 = 1 U 7 = 57 = 1 UDM‐12 (I1) I FW505 NA 12/17/1996 0:00 unknown GW µg/L 12 = 1 U 6 = 42 = 1 UDM‐12 (I1) I FW506 NA 12/17/1996 0:00 unknown GW µg/L 12 = 1 U 6 = 42 = 1 UDM‐12 (I1) I 931057‐5 NA 10/28/1993 0:00 unknown GW µg/L 8.6 = <0.2 3.1 = 70 = <0.2DM‐12 (I1) I 931057‐1 NA 10/28/1993 0:00 unknown GW µg/L 9.1 = <0.2 3.6 = 72 = <0.2DM‐12 (I1) I 931025‐1 NA 10/13/1993 0:00 unknown GW µg/L 5.3 = <0.2 1.6 = 53 = <0.2
DM‐13 (D1) NA 5/10/2020 0:00 unknownDM‐13 (D1) D1 FW586 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D1) D1 FQ878 NA 11/12/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D1) D1 FW502 NA 12/16/1996 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D1) D1 931116‐1 NA 11/5/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D1) D1 931116‐2 NA 11/5/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D1) D1 931040‐5 NA 10/19/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D1) D1 931039‐1 NA 10/18/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
DM‐13 (D2) NA 5/10/2020 0:00 unknownDM‐13 (D2) D2 FGS85 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FGS86 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FGF64 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FGF59 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FQ875 NA 11/12/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 970003‐9 NA 1/16/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U NDDM‐13 (D2) D2 931123‐5 NA 11/8/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 NDDM‐13 (D2) D2 931040‐4 NA 10/19/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D2) D2 931040‐6 NA 10/19/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
DM‐13 (I) NA 5/10/2020 0:00 unknownDM‐13 (I) I FGS87 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 10 = 5 U 5 U 48 = 5 UDM‐13 (I) I FW572 NA 2/1/2000 0:00 unknown GW µg/L 13 = 1 U 3 = 37 = 1 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 11 OF 72
011378
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
DM‐13 (I) I FGR83 NA 11/4/1999 0:00 unknown GW µg/L 15 = 2 U 6 = 47 = 2 UDM‐13 (I) I FGG00 NA 8/3/1999 0:00 unknown GW µg/L 12 = 1 U 3 = 64 = 1 UDM‐13 (I) I FGF99 NA 8/3/1999 0:00 unknown GW µg/L 13 = 1 U 3 = 69 = 1 UDM‐13 (I) I FQ880 NA 11/12/1997 0:00 unknown GW µg/L 11 = 1 U 2 = 86 = 1 UDM‐13 (I) I FQ879 NA 11/12/1997 0:00 unknown GW µg/L 10 = 5 U 5 U 76 = 5 UDM‐13 (I) I FW900 NA 12/16/1996 0:00 unknown GW µg/L 9 = 1 U 2 = 58 = 1 UDM‐13 (I) I 931057‐4 NA 10/28/1993 0:00 unknown GW µg/L 4.3 = <0.2 1 = 50 = <0.2DM‐13 (I) I 931040‐3 NA 10/19/1993 0:00 unknown GW µg/L 3.2 = <0.2 0.5 = 33 = <0.2
DM‐13 (S) NA 5/10/2020 0:00 unknownDM‐13 (S) S FX086 NA 5/2/2000 0:00 BAIL GW µg/L 2 = 2 = 1 = 3 = 1 UDM‐13 (S) S FW560 NA 2/9/2000 0:00 unknown GW µg/L 1 = 1 = 1 = 2 = 1 UDM‐13 (S) S FGR72 NA 11/3/1999 0:00 unknown GW µg/L 2 = 1 = 3 = 3 = 1 UDM‐13 (S) S FGF98 NA 8/3/1999 0:00 unknown GW µg/L 2 = 1 = 1 = 3 = 1 UDM‐13 (S) S FQ883 NA 11/12/1997 0:00 unknown GW µg/L 2 = 2 = 2 = 4 = 1 UDM‐13 (S) S FW899 NA 12/16/1996 0:00 unknown GW µg/L 2 = 2 = 3 = 4 = 1 UDM‐13 (S) S 931040‐2 NA 10/19/1993 0:00 unknown GW µg/L 2.6 = <0.2 2.4 = 6 = <0.2
FH‐MW4 (S) NA 5/10/2020 0:00 unknownFH‐MW4 (S) S FW580 NA 5/1/2000 0:00 BAIL GW µg/L 1 = 1 U 0.5 LJ 5 = 1 UFH‐MW4 (S) S FW581 NA 5/1/2000 0:00 BAIL GW µg/L 2 = 1 U 0.7 LJ 6 = 1 UFH‐MW4 (S) S FW550 NA 2/8/2000 0:00 unknown GW µg/L 1 = 1 U 0.6 LJ 5 = 1 UFH‐MW4 (S) S FGR61 NA 11/1/1999 0:00 unknown GW µg/L 2 = 1 U 2 = 5 = 1 UFH‐MW4 (S) S FGF71 NA 7/29/1999 0:00 unknown GW µg/L 1 = 1 U 0.7 LJ 5 = 1 U
FHMW‐5 (S) NA 5/10/2020 0:00 unknownFHMW‐5 (S) S FEF78 NA 8/5/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
FSB‐1 (S) NA 5/10/2020 0:00 unknownFSB‐1 (S) S FEF88 NA 8/12/1998 0:00 unknown GW µg/L 5 U 5 U 5 U 5 U 5 U
GP‐01 NA 5/10/2020 0:00 unknownGP‐01 unknown FW826 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐01 unknown FW827 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐02 unknown NA 5/10/2020 0:00 unknownGP‐02 unknown FW833 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐02 unknown FW830 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐03 unknown NA 5/10/2020 0:00 unknownGP‐03 unknown FW844 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐03 unknown FW845 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐03 unknown FW847 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐04 unknown NA 5/10/2020 0:00 unknownGP‐04 unknown FW837 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐04 unknown FW838 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐05 unknown NA 5/10/2020 0:00 unknown
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 12 OF 72
011379
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
GP‐05 unknown FW842 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐05 unknown FW843 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐06 unknown NA 5/10/2020 0:00 unknownGP‐06 unknown FW850 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
HSM‐I2‐4 NA 5/10/2020 0:00 unknownHSM‐I2‐4 I2 F3LW1 HSM‐I2‐4‐Q310 8/31/2010 15:15 PDB GW µg/L 2.6 = 0.5 U 0.76 = 8.8 = 0.5 UHSM‐I2‐4 I2 F1D95 HSM‐I2‐4 4/19/2005 13:05 LFS GW µg/L 4.3 = 1 U 1.1 = 15 = 1 U
HSM‐I2‐5 NA 5/10/2020 0:00 unknownHSM-I2-5 I2 HSM-I2-5-17-0814-FD HSM-I2-5-17 8/25/2014 9:57 PDB GW ug/L 6.4 = 0.5 U 1.0 = 25.5 = 0.5 UHSM-I2-5 I2 HSM-I2-5-17-0814 HSM-I2-5-17 8/25/2014 8:57 PDB GW ug/L 6.9 = 0.5 U 1.1 = 26.0 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐022014 HSM‐I2‐5‐17 2/18/2014 8:50 PDB GW µg/L 5.9 = 0.5 U 0.8 = 17.9 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐0813 HSM‐I2‐5‐17 8/12/2013 11:00 PDB GW µg/L 6.2 = 0.5 U 0.9 = 23.2 = 0.5 UHSM‐I2‐5 I2 F6PA9 HSM‐I2‐5‐17 2/12/2013 0:00 PDB GW µg/L 6.1 = 0.5 U 0.81 = 20 = 0.5 UHSM‐I2‐5 I2 F6CA2 HSM‐I2‐5‐17 8/20/2012 9:01 PDB GW µg/L 5.7 = 1.0 U 0.65 LJ 32 = 1.0 UHSM‐I2‐5 I2 F5G82 HSM‐I2‐5‐17 2/27/2012 12:30 PDB GW µg/L 5 = 0.5 U 0.73 = 20 = 0.5 UHSM‐I2‐5 I2 F4EA4 HSM‐I2‐5‐I2‐17‐Q311 8/22/2011 8:15 PDB GW µg/L 6.9 = 5.0 U 1.1 LJ 31 = 2.0 UHSM‐I2‐5 I2 HSM‐I2‐5‐I2‐17‐Q111 HSM‐I2‐5‐I2‐17 2/14/2011 8:11 PDB GW µg/L 5.2 = 0.5 U 0.6 = 25.6 = 0.5 UHSM‐I2‐5 I2 F3LW0 HSM‐I2‐5‐17‐Q310 8/30/2010 13:05 PDB GW µg/L 5.3 = 0.5 U 1.3 = 21 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17_100201 HSM‐I2‐5‐17 2/1/2010 12:35 PDB GW µg/L 6 = 0.5 U 1.2 = 31.2 = 0.5 UHSM‐I2‐5 I2 F3B61 HSM‐I2‐5‐17 10/26/2009 9:47 PDB GW µg/L 5.4 = 0.5 U 1.1 = 29 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐FD‐Q209 HSM‐I2‐5‐17‐FD 4/20/2009 8:47 PDB GW µg/L 6.8 = 0.5 U 1.2 = 40.2 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐Q209 HSM‐I2‐5‐17 4/20/2009 8:46 PDB GW µg/L 6.8 = 0.5 U 1.2 = 42.7 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐Q408 HSM‐I2‐5‐17 10/6/2008 10:36 PDB GW µg/L 7.5 = 0.5 U 1.4 = 41.8 = 0.5 UHSM‐I2‐5 I2 F2RY7 HSM‐I2‐5‐17 4/14/2008 0:00 PDB GW µg/L 9.2 = 0.5 U 2 = 71 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐Q407 HSM‐I2‐5‐17 10/1/2007 8:20 PDB GW µg/L 10.2 = 0.5 U 2.4 = 58 = 0.5 UHSM‐I2‐5 I2 HSM‐12‐5_070219 HSM‐I2‐5‐17 2/19/2007 8:00 PDB GW µg/L 10.2 JL 0.5 UJ 2.3 JL 72.8 JL 0.5 UJHSM‐I2‐5 I2 F2642DL HSM‐I2‐5‐17 8/29/2006 7:40 PDB GW µg/L 51 =HSM‐I2‐5 I2 F2642 HSM‐I2‐5‐17 8/29/2006 7:40 PDB GW µg/L 7.2 J 0.5 U 1 J 0.5 UHSM‐I2‐5 I2 F1YR1DL HSM‐I2‐5‐17 2/6/2006 8:45 PDB GW µg/L 62 =HSM‐I2‐5 I2 F1YR1 HSM‐I2‐5‐17 2/6/2006 8:45 PDB GW µg/L 7.3 = 0.5 U 0.99 = 0.5 UHSM‐I2‐5 I2 F1YR0DL HSM‐I2‐5‐12 2/6/2006 8:43 PDB GW µg/L 36 =HSM‐I2‐5 I2 F1YR0 HSM‐I2‐5‐12 2/6/2006 8:43 PDB GW µg/L 7 J 0.5 U 1.1 = 0.5 UHSM‐I2‐5 I2 F1P16DL HSM‐I2‐5‐12 7/13/2005 8:38 PDB GW µg/L 74 =HSM‐I2‐5 I2 F1P16 HSM‐I2‐5‐12 7/13/2005 8:38 PDB GW µg/L 9.6 = 0.5 U 1.6 = 0.5 UHSM‐I2‐5 I2 F1P17DL HSM‐I2‐5‐17 7/13/2005 8:36 PDB GW µg/L 95 =HSM‐I2‐5 I2 F1P17 HSM‐I2‐5‐17 7/13/2005 8:36 PDB GW µg/L 13 = 0.5 U 1.9 = 0.5 UHSM‐I2‐5 I2 F1P15DL HSM‐I2‐5‐7 7/13/2005 8:32 PDB GW µg/L 61 =HSM‐I2‐5 I2 F1P15 HSM‐I2‐5‐7 7/13/2005 8:32 PDB GW µg/L 9.9 = 0.5 U 1.6 = 0.3 LJHSM‐I2‐5 I2 F1P14DL HSM‐I2‐5‐2 7/13/2005 8:29 PDB GW µg/L 34 =HSM‐I2‐5 I2 F1P14 HSM‐I2‐5‐2 7/13/2005 8:29 PDB GW µg/L 7.5 = 0.5 U 1.2 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 13 OF 72
011380
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
HSM‐I2‐5 I2 F1D93DL HSM‐I2‐5 4/19/2005 9:30 LFS GW µg/L 59 =HSM‐I2‐5 I2 F1D93 HSM‐I2‐5 4/19/2005 9:30 LFS GW µg/L 11 = 0.5 U 1.6 = 0.26 LJHSM‐I2‐5 I2 F1DC1DL HSM‐I2‐5‐17 4/19/2005 8:38 PDB GW µg/L 99 =HSM‐I2‐5 I2 F1DC1 HSM‐I2‐5‐17 4/19/2005 8:38 PDB GW µg/L 16 = 0.5 U 2.1 = 0.36 LJHSM‐I2‐5 I2 F1DC0 HSM‐I2‐5‐12 4/19/2005 8:36 PDB GW µg/L 9.8 = 4.2 U 2 LJ 73 = 4.2 UHSM‐I2‐5 I2 F1DB9 HSM‐I2‐5‐7 4/19/2005 8:30 PDB GW µg/L 11 = 2.5 U 1.8 LJ 45 J 2.5 UHSM‐I2‐5 I2 F1DB8DL HSM‐I2‐5‐2 4/19/2005 8:27 PDB GW µg/L 65 =HSM‐I2‐5 I2 F1DB8 HSM‐I2‐5‐2 4/19/2005 8:27 PDB GW µg/L 11 = 0.5 U 1.6 = 0.25 LJHSM‐I2‐5 I2 F1808DL HSM‐I2‐5 11/15/2004 11:30 LFS GW µg/L 54 =HSM‐I2‐5 I2 F1808 HSM‐I2‐5 11/15/2004 11:30 LFS GW µg/L 9.6 = 0.5 U 1.6 = 0.5 UHSM‐I2‐5 I2 F1812DL HSM‐I2‐5‐17 11/15/2004 10:54 PDB GW µg/L 86 =HSM‐I2‐5 I2 F1812 HSM‐I2‐5‐17 11/15/2004 10:54 PDB GW µg/L 13 = 0.5 U 1.6 = 0.5 UHSM‐I2‐5 I2 F1811DL HSM‐I2‐5‐12 11/15/2004 10:52 PDB GW µg/L 71 =HSM‐I2‐5 I2 F1811 HSM‐I2‐5‐12 11/15/2004 10:52 PDB GW µg/L 9.8 = 0.5 U 1.4 = 0.5 UHSM‐I2‐5 I2 F1810DL HSM‐I2‐5‐7 11/15/2004 10:50 PDB GW µg/L 69 =HSM‐I2‐5 I2 F1810 HSM‐I2‐5‐7 11/15/2004 10:50 PDB GW µg/L 9.9 = 0.5 U 1.4 = 0.5 UHSM‐I2‐5 I2 F1809DL HSM‐I2‐5‐2 11/15/2004 10:48 PDB GW µg/L 69 =HSM‐I2‐5 I2 F1809 HSM‐I2‐5‐2 11/15/2004 10:48 PDB GW µg/L 9.6 = 0.5 U 1.4 = 0.5 UHSM‐I2‐5 I2 F0NF9 HSM‐I2‐5‐104 12/3/2003 14:14 PDB GW µg/L 5 = 0.5 U 0.7 = 0.5 UHSM‐I2‐5 I2 F0NF9DL HSM‐I2‐5‐104 12/3/2003 14:14 PDB GW µg/L 29 =HSM‐I2‐5 I2 F0NF8 HSM‐I2‐5‐99 12/3/2003 14:10 PDB GW µg/L 3.8 = 0.5 U 0.53 = 23 = 0.5 UHSM‐I2‐5 I2 F0NF7 HSM‐I2‐5‐94 12/3/2003 14:08 PDB GW µg/L 4.7 = 0.5 U 0.71 = 0.5 UHSM‐I2‐5 I2 F0NF7DL HSM‐I2‐5‐94 12/3/2003 14:08 PDB GW µg/L 21 =HSM‐I2‐5 I2 F0NF6 HSM‐I2‐5‐89 12/3/2003 14:05 PDB GW µg/L 3.7 = 0.5 U 0.58 = 20 = 0.5 UHSM‐I2‐5 I2 HSMI25Q403 HSMI25Q403 11/13/2003 10:43 unknown GW µg/L 7.2 = 0.7936 < 45 = 0.2227 <
McDonalds (D2) NA 5/10/2020 0:00 unknownMcDonalds (D2) D2 McDonalds-D2-2-0814 McDonalds-D2-2 8/25/2014 8:28 PDB GW ug/L 0.8 = 0.5 U 0.5 U 6.3 = 0.5 UMcDonalds (D2) D2 McDonalds-D2-5-0814 McDonalds-D2-5 8/25/2014 8:25 PDB GW ug/L 0.8 = 0.5 U 0.5 U 5.0 = 0.5 UMcDonalds (D2) D2 McDonalds-D2-8-0814 McDonalds-D2-8 8/25/2014 8:20 PDB GW ug/L 0.9 = 0.5 U 0.5 U 5.1 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐8‐022014 McDonalds‐D2‐2 2/17/2014 8:10 PDB GW µg/L 2.1 = 0.5 U 1.2 = 6.6 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐5‐022014 McDonalds‐D2‐5 2/17/2014 8:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.8 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐2‐022014 McDonalds‐D2‐8 2/17/2014 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.6 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐8‐0813 McDonalds‐D2‐8 8/12/2013 12:35 PDB GW µg/L 3 = 0.5 U 2.2 = 9.2 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐5‐0813 McDonalds‐D2‐5 8/12/2013 12:30 PDB GW µg/L 0.7 = 0.5 U 0.5 = 3.6 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐2‐0813 McDonalds‐D2‐2 8/12/2013 12:25 PDB GW µg/L 0.9 = 0.5 U 0.5 U 6.6 = 0.5 UMcDonalds (D2) D2 F6PB1 McDonalds‐D2‐5 2/18/2013 0:00 PDB GW µg/L 3.3 = 0.26 LJ 2.3 = 10 = 0.5 UMcDonalds (D2) D2 F6PB0 McDonalds‐D2‐2 2/18/2013 0:00 PDB GW µg/L 0.74 = 0.5 U 0.41 LJ 3.9 = 0.5 UMcDonalds (D2) D2 F6PB2 McDonalds‐D2‐8 2/18/2013 0:00 PDB GW µg/L 3.8 = 0.5 U 4.7 = 6 = 0.5 UMcDonalds (D2) D2 F6CD5 McDonalds‐D2‐8 8/20/2012 12:40 PDB GW µg/L 3.4 = 0.16 LJ 2.5 = 8.7 = 0.5 UMcDonalds (D2) D2 F6CD4 McDonalds‐D2‐5 8/20/2012 12:38 PDB GW µg/L 0.71 = 0.040 LJ 0.38 LJ 3.3 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 14 OF 72
011381
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
McDonalds (D2) D2 F6CD3 McDonalds‐D2‐2 8/20/2012 12:37 PDB GW µg/L 1.6 = 0.041 LJ 0.80 = 11 = 0.5 UMcDonalds (D2) D2 F5G07 McDonalds‐D2‐2 2/27/2012 13:33 PDB GW µg/L 0.45 LJ 0.5 U 0.14 LJ 3.3 = 0.5 UMcDonalds (D2) D2 F5G08 McDonalds‐D2‐5 2/27/2012 13:30 PDB GW µg/L 1.9 = 0.5 U 0.82 = 8 = 0.5 UMcDonalds (D2) D2 F5G09 McDonalds‐D2‐8 2/27/2012 13:28 PDB GW µg/L 2.4 = 0.5 U 2.3 = 5.8 = 0.5 UMcDonalds (D2) D2 F4EA7 Mcdonalds‐D2‐12‐Q311 8/22/2011 13:40 PDB GW µg/L 2.8 LJ 5.0 U 1.1 LJ 11 = 2.0 UMcDonalds (D2) D2 F4EA6 Mcdonalds‐D2‐7‐Q311 8/22/2011 13:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 3.5 LJ 2.0 UMcDonalds (D2) D2 F4EA5 Mcdonalds‐D2‐2‐Q311 8/22/2011 13:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 4.7 LJ 2.0 UMcDonalds (D2) D2 F3S11 McDonalds‐D2‐12 2/15/2011 11:55 PDB GW µg/L 0.3 LJ 0.5 U 0.5 U 0.74 = 0.5 UMcDonalds (D2) D2 F3S10 McDonalds‐D2‐12 2/15/2011 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMcDonalds (D2) D2 F3S09 McDonalds‐D2‐7 2/15/2011 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMcDonalds (D2) D2 F3S08 McDonalds‐D2‐2 2/15/2011 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMcDonalds (D2) D2 FGS98 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 0.5 LJ 1 U 1 U 1 = 1 UMcDonalds (D2) D2 FW547 NA 2/8/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
MNW‐01 (I2) NA 5/10/2020 0:00 unknownMNW-01 (I2) I2 MNW-1-I2-7-0814 MNW-1-I2-7 8/25/2014 8:15 PDB GW ug/L 4.3 = 0.5 U 1.3 = 19.7 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐022014‐FD MNW‐1‐I2‐7 2/17/2014 9:20 PDB GW µg/L 3.8 = 0.5 U 0.9 = 17.8 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐022014 MNW‐1‐I2‐7 2/17/2014 8:20 PDB GW µg/L 4.1 = 0.5 U 1 = 19 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐0813 MNW‐1‐I2‐7 8/13/2013 9:00 PDB GW µg/L 3.7 = 0.5 U 0.6 = 22.4 = 0.5 UMNW‐01 (I2) I2 F6PF0 MNW‐1‐I2‐7 2/18/2013 0:00 PDB GW µg/L 2.7 = 0.5 U 0.22 LJ 13 = 0.5 UMNW‐01 (I2) I2 F6CA3 MNW‐1‐I2‐7 8/20/2012 9:38 PDB GW µg/L 3.4 = 1.0 U 0.29 LJ 17 = 1.0 UMNW‐01 (I2) I2 F5G86 MNW‐1‐I2‐7 2/28/2012 8:20 PDB GW µg/L 2.6 = 0.5 U 0.5 U 14 = 0.5 UMNW‐01 (I2) I2 F4EC4 MNW‐1‐I2‐7‐FD‐Q311 8/23/2011 7:59 PDB GW µg/L 3.5 LJ 5.0 U 5.0 U 18 = 2.0 UMNW‐01 (I2) I2 F4EC3 MNW‐1‐I2‐7‐Q311 8/23/2011 7:57 PDB GW µg/L 2.9 LJ 5.0 U 5.0 U 15 = 2.0 UMNW‐01 (I2) I2 MNW‐1‐I2‐5‐Q111 MNW‐1‐I2‐7 2/16/2011 8:25 PDB GW µg/L 1.9 = 0.5 U 0.5 U 10.7 JH 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q310‐FD MNW‐1‐I2‐7‐Q310‐FD 9/8/2010 8:30 PDB GW µg/L 2.1 = 0.5 U 0.5 U 9.2 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q310 MNW‐1‐I2‐7‐Q310 9/8/2010 8:25 PDB GW µg/L 2.0 = 0.5 U 0.5 U 10.2 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7_100201 MNW‐1‐I2‐7 2/1/2010 7:45 PDB GW µg/L 1.9 = 0.5 U 0.5 U 8.4 = 0.5 UMNW‐01 (I2) I2 F3B18 MNW‐1‐I2‐7 10/26/2009 9:02 PDB GW µg/L 1.7 = 0.5 U 0.5 U 8.4 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q209 MNW‐1‐I2‐7 4/20/2009 8:02 PDB GW µg/L 2.3 = 0.5 U 0.5 U 12.7 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q408 MNW‐1‐I2‐7 10/6/2008 8:10 PDB GW µg/L 2.4 = 0.5 U 0.5 U 12.8 = 0.5 UMNW‐01 (I2) I2 F2643 MNW‐1‐I2‐7 8/29/2006 7:20 PDB GW µg/L 0.97 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐01 (I2) I2 F1NN6 MNW‐1‐I2‐17 7/12/2005 10:51 PDB GW µg/L 1.2 = 0.5 U 0.5 U 2.2 = 0.5 UMNW‐01 (I2) I2 F1NN5 MNW‐1‐I2‐12 7/12/2005 10:49 PDB GW µg/L 1.3 = 0.5 U 0.17 LJ 2.3 = 0.1 LJMNW‐01 (I2) I2 F1NN3 MNW‐1‐I2‐7 7/12/2005 10:48 PDB GW µg/L 0.9 = 0.5 U 0.19 LJ 2.7 = 0.5 UMNW‐01 (I2) I2 F1NN2 MNW‐1‐I2‐2 7/12/2005 10:47 PDB GW µg/L 0.86 = 0.5 U 0.19 LJ 2.7 = 0.5 UMNW‐01 (I2) I2 F1DJ7 MNW‐1‐I2‐17 4/20/2005 8:41 PDB GW µg/L 0.81 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐01 (I2) I2 F1DJ6 MNW‐1‐I2‐12 4/20/2005 8:38 PDB GW µg/L 0.74 = 0.5 U 0.5 U 1.5 = 0.5 UMNW‐01 (I2) I2 F1DJ4 MNW‐1‐I2‐7 4/20/2005 8:33 PDB GW µg/L 0.75 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐01 (I2) I2 F1DJ3 MNW‐1‐I2‐2 4/20/2005 8:29 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐01 (I2) I2 F17G9 MNW‐1‐I2‐17 11/9/2004 8:40 PDB GW µg/L 1.9 = 0.5 U 0.5 U 2.6 = 0.25 LJ
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 15 OF 72
011382
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐01 (I2) I2 F17G8 MNW‐1‐I2‐12 11/9/2004 8:33 PDB GW µg/L 2 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐01 (I2) I2 F17G7 MNW‐1‐I2‐7 11/9/2004 8:26 PDB GW µg/L 1.7 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐01 (I2) I2 F17G6 MNW‐1‐I2‐2 11/9/2004 8:18 PDB GW µg/L 1.7 = 0.5 U 0.5 U 2.1 = 0.5 UMNW‐01 (I2) I2 MNW1Q403 MNW1Q403 11/16/2003 11:35 unknown GW µg/L 3.9 = 0.7936 < 10 = 0.4 J
MNW‐02 (I2) 5/10/2020 0:00 unknownMNW‐02 (I2) I2 F6PF1 MNW‐2‐I2‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F3S45 MNW‐2‐I2‐7 2/15/2011 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 MNW‐2‐I2‐7‐Q209 MNW‐2‐I2‐7 4/20/2009 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 MNW‐2‐I2‐7‐Q407 MNW‐2‐I2‐7 10/2/2007 8:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1P00 MNW‐2‐I2‐17 7/13/2005 8:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1NZ9 MNW‐2‐I2‐12 7/13/2005 8:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1NZ8 MNW‐2‐I2‐7 7/13/2005 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1NZ7 MNW‐2‐I2‐2 7/13/2005 8:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT3 MNW‐2‐I2‐17 4/20/2005 13:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT2 MNW‐2‐I2‐12 4/20/2005 13:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT1 MNW‐2‐I2‐7 4/20/2005 13:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT0 MNW‐2‐I2‐2 4/20/2005 13:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17D3 MNW‐2‐I2 11/17/2004 8:40 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17J0 MNW‐2‐I2‐17 11/8/2004 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17H9 MNW‐2‐I2‐12 11/8/2004 11:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17H8 MNW‐2‐I2‐7 11/8/2004 11:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17H7 MNW‐2‐I2‐2 11/8/2004 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 MNW2Q403 MNW2Q403 11/15/2003 11:42 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐03 (D1) 5/10/2020 0:00 unknownMNW‐03 (D1) D1 F6PF2 MNW‐3‐D1‐7 2/18/2013 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F3S19 MNW‐3‐D1‐7 2/15/2011 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 MNW‐3‐D1‐7‐Q209 MNW‐3‐D1‐7 4/21/2009 14:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐03 (D1) D1 MNW‐3‐D1‐7‐Q407 MNW‐3‐D1‐7 10/2/2007 8:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1P04 MNW‐3‐D1‐17 7/12/2005 11:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1P03 MNW‐3‐D1‐12 7/12/2005 11:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1P02 MNW‐3‐D1‐7 7/12/2005 11:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1P01 MNW‐3‐D1‐2 7/12/2005 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT7 MNW‐3‐D1‐17 4/20/2005 14:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT6 MNW‐3‐D1‐12 4/20/2005 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT5 MNW‐3‐D1‐7 4/20/2005 13:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT4 MNW‐3‐D1‐2 4/20/2005 13:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17N1 MNW‐3‐D1‐17 11/8/2004 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17M9 MNW‐3‐D1‐12 11/8/2004 10:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17M8 MNW‐3‐D1‐7 11/8/2004 10:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17M7 MNW‐3‐D1‐2 11/8/2004 9:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 16 OF 72
011383
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐03 (D1) D1 MNW3D1Q403 MNW3D1Q403 11/18/2003 14:52 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <MNW‐03 (D2) 5/10/2020 0:00 unknown
MNW‐03 (D2) D2 F6PF3 MNW‐3‐D2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJvMNW‐03 (D2) D2 F3S21 MNW‐3‐D2‐7 2/15/2011 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐03 (D2) D2 F3S20 MNW‐3‐D2‐7 2/15/2011 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐03 (D2) D2 MNW‐3‐D2‐7‐Q209 MNW‐3‐D2‐7 4/21/2009 14:05 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐03 (D2) D2 MNW‐3‐D2‐7‐Q407 MNW‐3‐D2‐7 10/2/2007 8:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P08 MNW‐3‐D2‐17 7/12/2005 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P07 MNW‐3‐D2‐12 7/12/2005 11:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P06 MNW‐3‐D2‐7 7/12/2005 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P05 MNW‐3‐D2‐2 7/12/2005 10:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DW1 MNW‐3‐D2‐17 4/20/2005 14:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DW0 MNW‐3‐D2‐12 4/20/2005 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DT9 MNW‐3‐D2‐7 4/20/2005 14:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DT8 MNW‐3‐D2‐2 4/20/2005 14:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17D4 MNW‐3‐D2 11/8/2004 11:54 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N2 MNW‐3‐D2‐2 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N3 MNW‐3‐D2‐7 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N4 MNW‐3‐D2‐12 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N5 MNW‐3‐D2‐17 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 MNW3D2Q403 MNW3D2Q403 11/19/2003 9:35 unknown GW µg/L 0.2937 <
MNW‐03 (D3) 5/10/2020 0:00 unknownMNW‐03 (D3) D3 F6PF4 MNW‐3‐D3‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F3S22 MNW‐3‐D3‐7 2/15/2011 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.31 LJ 0.5 UMNW‐03 (D3) D3 MNW‐3‐D3‐7‐Q209 MNW‐3‐D3‐7 4/21/2009 14:15 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐03 (D3) D3 MNW‐3‐D3‐7‐Q407 MNW‐3‐D3‐7 10/2/2007 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P13 MNW‐3‐D3‐17 7/12/2005 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P12 MNW‐3‐D3‐12 7/12/2005 10:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P11 MNW‐3‐D3‐7 7/12/2005 10:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P09 MNW‐3‐D3‐2 7/12/2005 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW6 MNW‐3‐D3‐17 4/20/2005 14:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW5 MNW‐3‐D3‐12 4/20/2005 14:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW4 MNW‐3‐D3‐7 4/20/2005 14:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW2 MNW‐3‐D3‐2 4/20/2005 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F17P0 MNW‐3‐D3‐17 11/8/2004 10:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.22 LJMNW‐03 (D3) D3 F17N9 MNW‐3‐D3‐12 11/8/2004 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F17N8 MNW‐3‐D3‐7 11/8/2004 10:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F17N6 MNW‐3‐D3‐2 11/8/2004 10:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 MNW3D3Q403 MNW3D3Q403 11/19/2003 16:12 unknown GW µg/L 0.2937 <
MNW‐04 (D1) 5/10/2020 0:00 unknown
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 17 OF 72
011384
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐04 (D1) D1 MNW‐4‐D1‐12‐022014 MNW‐4‐D1‐12 2/18/2014 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F6PF5 MNW‐4‐D1‐12 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.3 LJ 0.5 UMNW‐04 (D1) D1 F5G31 MNW‐4‐D1‐12 2/28/2012 13:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F3S23 MNW‐4‐D1‐12 2/15/2011 7:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.35 LJ 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12_100201‐FD MNW‐4‐D1‐12 2/1/2010 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12_100201 MNW‐4‐D1‐12 2/1/2010 8:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12‐Q209 MNW‐4‐D1‐12 4/20/2009 12:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12‐Q408 MNW‐4‐D1‐12 10/6/2008 12:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F2RQ1 MNW‐4‐D1‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12‐Q407 MNW‐4‐D1‐12 10/2/2007 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1_070219 MNW‐4‐D1‐12 2/19/2007 8:05 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐04 (D1) D1 F2675 MNW‐4‐D1‐12 8/28/2006 13:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1YR4 MNW‐4‐D1‐12 2/6/2006 8:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1P73 MNW‐4‐D1‐17 7/12/2005 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UMNW‐04 (D1) D1 F1P72 MNW‐4‐D1‐12 7/12/2005 10:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 UMNW‐04 (D1) D1 F1P71 MNW‐4‐D1‐7 7/12/2005 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.17 LJ 0.5 UMNW‐04 (D1) D1 F1P70 MNW‐4‐D1‐2 7/12/2005 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1E21 MNW‐4‐D1‐17 4/18/2005 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.1 LJ 0.5 UMNW‐04 (D1) D1 F1E20 MNW‐4‐D1‐12 4/18/2005 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.11 LJ 0.5 UMNW‐04 (D1) D1 F1E19 MNW‐4‐D1‐7 4/18/2005 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1E18 MNW‐4‐D1‐2 4/18/2005 10:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P4 MNW‐4‐D1‐17 11/8/2004 12:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P3 MNW‐4‐D1‐12 11/8/2004 12:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P2 MNW‐4‐D1‐7 11/8/2004 12:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P1 MNW‐4‐D1‐2 11/8/2004 12:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW4D1Q403 MNW4D1Q403 12/5/2003 9:32 unknown GW µg/L 0.7 J 1.1 = 2.4 = 0.2227 <
MNW‐04 (D2) 5/10/2020 0:00 unknownMNW-04 (D2) D2 MNW-4-D2-7-0814 MNW-4-D2-7 8/25/2014 11:05 PDB GW ug/L 3.4 = 0.5 U 0.7 = 3.1 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐022014 MNW‐4‐D2‐7 2/18/2014 9:47 PDB GW µg/L 2.8 = 0.5 U 0.6 = 2.6 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐0813 MNW‐4‐D2‐7 8/12/2013 10:55 PDB GW µg/L 2.3 = 0.5 U 0.5 U 2.3 = 0.5 UMNW‐04 (D2) D2 F6PF6 MNW‐4‐D2‐7 2/13/2013 0:00 PDB GW µg/L 2.3 = 0.5 U 0.37 LJ 2.1 = 0.5 UMNW‐04 (D2) D2 F5G32 MNW‐4‐D2‐7 2/28/2012 13:15 PDB GW µg/L 0.96 UM 0.5 U 0.19 LJ 1.4 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q111 MNW‐4‐D2‐7 3/24/2011 10:20 PDB GW µg/L 0.5 = 0.5 U 0.5 U 1.2 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7_100201‐FD MNW‐4‐D2‐7 2/1/2010 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.9 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7_100201 MNW‐4‐D2‐7 2/1/2010 9:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐FD‐Q209 MNW‐4‐D2‐7‐FD 4/20/2009 13:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q209 MNW‐4‐D2‐7 4/20/2009 13:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q408 MNW‐4‐D2‐7 10/6/2008 12:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F2RQ2 MNW‐4‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.59 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q407 MNW‐4‐D2‐7 10/2/2007 10:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 18 OF 72
011385
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐04 (D2) D2 MNW‐4‐D2_070219 MNW‐4‐D2‐7 2/19/2007 8:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐04 (D2) D2 F2676 MNW‐4‐D2‐7 8/28/2006 13:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F1YR5 MNW‐4‐D2‐7 2/6/2006 8:36 PDB GW µg/L 4.9 = 0.5 U 1.3 = 13 = 0.5 UMNW‐04 (D2) D2 F1P78 MNW‐4‐D2‐17 7/12/2005 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UMNW‐04 (D2) D2 F1P77 MNW‐4‐D2‐12 7/12/2005 10:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F1P76 MNW‐4‐D2‐7 7/12/2005 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UMNW‐04 (D2) D2 F1P75 MNW‐4‐D2‐2 7/12/2005 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.21 LJ 0.5 UMNW‐04 (D2) D2 F1E26 MNW‐4‐D2‐17 4/18/2005 11:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UMNW‐04 (D2) D2 F1E25 MNW‐4‐D2‐12 4/18/2005 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.24 LJ 0.5 UMNW‐04 (D2) D2 F1E24 MNW‐4‐D2‐7 4/18/2005 11:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.21 LJ 0.5 UMNW‐04 (D2) D2 F1E23 MNW‐4‐D2‐2 4/18/2005 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.17 LJ 0.5 UMNW‐04 (D2) D2 F17D5 MNW‐4‐D2 11/16/2004 12:15 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.35 LJ 0.5 UMNW‐04 (D2) D2 F17P9 MNW‐4‐D2‐17 11/8/2004 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F17P8 MNW‐4‐D2‐12 11/8/2004 14:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F17P7 MNW‐4‐D2‐7 11/8/2004 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F17P6 MNW‐4‐D2‐2 11/8/2004 13:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 MNW4D2Q403 MNW4D2Q403 12/6/2003 11:33 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐04 (D3) 5/10/2020 0:00 unknownMNW‐04 (D3) D3 MNW‐4‐D3‐7‐022014 MNW‐4‐D3‐7 2/18/2014 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F6PF7 MNW‐4‐D3‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F5G33 MNW‐4‐D3‐7 2/28/2012 12:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F3S25 MNW‐4‐D3‐7 2/15/2011 8:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7_100201 MNW‐4‐D3‐7 2/1/2010 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7‐Q209 MNW‐4‐D3‐7 4/20/2009 12:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7‐Q408 MNW‐4‐D3‐7 10/6/2008 13:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F2RQ3 MNW‐4‐D3‐7 4/14/2008 0:00 PDB GW µg/L 6.9 = 0.29 LJ 3.1 = 9 = 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7‐Q407 MNW‐4‐D3‐7 10/2/2007 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3_070219 MNW‐4‐D3‐7 2/19/2007 8:38 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐04 (D3) D3 F2677 MNW‐4‐D3‐7 8/28/2006 13:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1YR7 MNW‐4‐D3‐17 2/6/2006 8:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1YR6 MNW‐4‐D3‐7 2/6/2006 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P82 MNW‐4‐D3‐17 7/12/2005 11:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P81 MNW‐4‐D3‐12 7/12/2005 11:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P80 MNW‐4‐D3‐7 7/12/2005 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P79 MNW‐4‐D3‐2 7/12/2005 11:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E30 MNW‐4‐D3‐17 4/18/2005 12:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E29 MNW‐4‐D3‐12 4/18/2005 12:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E28 MNW‐4‐D3‐7 4/18/2005 12:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E27 MNW‐4‐D3‐2 4/18/2005 12:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐04 (D3) D3 F17Q3 MNW‐4‐D3‐17 11/8/2004 13:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 19 OF 72
011386
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐04 (D3) D3 F17Q2 MNW‐4‐D3‐12 11/8/2004 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F17Q1 MNW‐4‐D3‐7 11/8/2004 13:15 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐04 (D3) D3 F17Q0 MNW‐4‐D3‐2 11/8/2004 13:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW4D3Q403 MNW4D3Q403 12/3/2003 11:50 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐05 (D1) 5/10/2020 0:00 unknownMNW-05 (D1) D1 MNW-5-D1-12-0814 MNW-5-D1-12 8/25/2014 9:19 PDB GW ug/L 3.1 = 0.5 U 1.3 = 3.6 = 0.5 UMNW-05 (D1) D1 MNW-5-D1-7-0814 MNW-5-D1-7 8/25/2014 9:15 PDB GW ug/L 5.6 = 1.4 = 2.3 = 9.7 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐022014 MNW‐5‐D1‐12 2/18/2014 12:07 PDB GW µg/L 3.6 = 0.5 U 1.6 = 4.4 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐022014 MNW‐5‐D1‐7 2/18/2014 12:05 PDB GW µg/L 5.6 = 1.2 = 2.2 = 8.9 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐0813 MNW‐5‐D1‐12 8/13/2013 9:10 PDB GW µg/L 3.9 = 0.5 U 2.1 = 5.2 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐0813FD MNW‐5‐D1‐7 8/13/2013 9:05 PDB GW µg/L 5.4 = 1.2 = 1.9 = 7.8 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐0813 MNW‐5‐D1‐7 8/13/2013 9:00 PDB GW µg/L 5.4 = 1.4 = 2.3 = 9 = 0.5 UMNW‐05 (D1) D1 F6PF9 MNW‐5‐D1‐12‐FD 2/13/2013 0:00 PDB GW µg/L 4.2 = 0.18 LJ 1.6 = 4.8 = 0.5 UMNW‐05 (D1) D1 F6PF8 MNW‐5‐D1‐12 2/13/2013 0:00 PDB GW µg/L 4.1 = 0.19 LJ 1.6 = 4.9 = 0.5 UMNW‐05 (D1) D1 F6PG0 MNW‐5‐D1‐7 2/13/2013 0:00 PDB GW µg/L 5.8 = 1.1 = 2.1 = 8.4 = 0.5 UMNW‐05 (D1) D1 F6CD6 MNW‐5‐D1‐12 8/20/2012 12:03 PDB GW µg/L 3.6 = 0.16 LJ 1.4 = 4.6 = 0.5 UMNW‐05 (D1) D1 F6CD7 MNW‐5‐D1‐7 8/20/2012 12:02 PDB GW µg/L 5.2 = 0.87 = 1.7 = 7.7 = 0.5 UMNW‐05 (D1) D1 F5G34 MNW‐5‐D1‐12 2/28/2012 10:29 PDB GW µg/L 2.9 = 0.5 U 1.3 = 4.3 = 0.5 UMNW‐05 (D1) D1 F5G35 MNW‐5‐D1‐7 2/28/2012 10:27 PDB GW µg/L 4 = 0.69 = 1.4 = 6.9 = 0.5 UMNW‐05 (D1) D1 F4EC5 MNW‐5‐D1‐12‐Q311 8/22/2011 11:22 PDB GW µg/L 4.6 LJ 5.0 U 2.2 LJ 6.1 = 2.0 UMNW‐05 (D1) D1 F4EC6 MNW‐5‐D1‐7‐Q311 8/22/2011 11:20 PDB GW µg/L 5.3 = 5.0 U 2.0 LJ 8.4 = 2.0 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q111 MNW‐5‐D1‐12 2/14/2011 9:07 PDB GW µg/L 2.7 = 0.5 U 1.5 = 3.8 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q111 MNW‐5‐D1‐7 2/14/2011 9:06 PDB GW µg/L 3.6 = 0.5 U 1.6 = 5.2 = 0.5 UMNW‐05 (D1) D1 F3LQ4 MNW‐5‐D1‐12‐Q310 9/2/2010 9:00 PDB GW µg/L 2.7 = 0.5 U 1.5 = 3.8 = 0.5 UMNW‐05 (D1) D1 F3LQ3 MNW‐5‐D1‐7‐Q310 9/2/2010 8:55 PDB GW µg/L 2.9 = 0.5 U 1.5 = 4.1 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12_100201 MNW‐5‐D1‐12 2/1/2010 13:17 PDB GW µg/L 3.5 = 0.5 U 1.8 = 4.9 = 0.5 UMNW‐05 (D1) D1 F3B19 MNW‐5‐D1‐7 10/27/2009 8:10 PDB GW µg/L 4.1 = 0.5 U 1.8 = 4.9 = 0.5 UMNW‐05 (D1) D1 F3B20 MNW‐5‐D1‐12 10/27/2009 8:06 PDB GW µg/L 4.2 = 0.5 U 2 = 5.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q209 MNW‐5‐D1‐7 4/20/2009 9:14 PDB GW µg/L 4.6 = 0.5 = 2.0 = 7.2 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q209 MNW‐5‐D1‐12 4/20/2009 9:03 PDB GW µg/L 4.4 = 0.5 U 2.0 = 6.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q408 MNW‐5‐D1‐12 10/7/2008 9:06 PDB GW µg/L 5 = 0.5 U 2.4 = 7.0 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q408 MNW‐5‐D1‐7 10/7/2008 9:02 PDB GW µg/L 5 = 0.5 U 2.3 = 6.8 = 0.5 UMNW‐05 (D1) D1 F2RQ5 MNW‐5‐D1‐12 4/14/2008 0:00 PDB GW µg/L 12 = 0.71 = 4.9 = 19 = 0.5 UMNW‐05 (D1) D1 F2RQ4 MNW‐5‐D1‐7 4/14/2008 0:00 PDB GW µg/L 5.8 = 0.5 U 2.6 = 7.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q407 MNW‐5‐D1‐7 10/1/2007 10:40 PDB GW µg/L 5.8 = 0.5 U 2.7 = 7.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q407 MNW‐5‐D1‐12 10/1/2007 10:33 PDB GW µg/L 5.5 = 0.5 U 2.4 = 7.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12_070219 MNW‐5‐D1‐12 2/19/2007 9:19 PDB GW µg/L 5.6 JL 0.5 UJ 2.7 JL 9.0 JL 0.5 UJMNW‐05 (D1) D1 MNW‐5‐D1‐7_070219 MNW‐5‐D1‐7 2/19/2007 9:14 PDB GW µg/L 6 JL 0.5 UJ 2.9 JL 9.7 JL 0.5 UJMNW‐05 (D1) D1 F2678 MNW‐5‐D1‐12 8/28/2006 10:20 PDB GW µg/L 5.2 = 0.5 U 2.1 = 7.3 = 0.5 UMNW‐05 (D1) D1 F2679 MNW‐5‐D1‐7 8/28/2006 10:10 PDB GW µg/L 5.2 = 0.5 U 2 = 7.5 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 20 OF 72
011387
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐05 (D1) D1 F1YT7 MNW‐5‐D1‐12 2/6/2006 10:23 PDB GW µg/L 6.7 = 0.5 U 2.8 = 9.2 = 0.5 UMNW‐05 (D1) D1 F1YT6 MNW‐5‐D1‐7 2/6/2006 10:20 PDB GW µg/L 6.3 = 0.61 = 2.5 = 8.6 = 0.5 UMNW‐05 (D1) D1 F1P39 MNW‐5‐D1‐17 7/11/2005 11:21 PDB GW µg/L 8.2 = 0.4 LJ 3.6 = 11 J 0.2 LJMNW‐05 (D1) D1 F1P38 MNW‐5‐D1‐12 7/11/2005 11:20 PDB GW µg/L 8.3 = 0.43 LJ 3.7 = 11 = 0.2 LJMNW‐05 (D1) D1 F1P36 MNW‐5‐D1‐7 7/11/2005 11:15 PDB GW µg/L 7.2 = 0.39 LJ 3.1 = 10 = 0.18 LJMNW‐05 (D1) D1 F1P35 MNW‐5‐D1‐2 7/11/2005 11:14 PDB GW µg/L 7.5 = 0.59 = 3.4 = 11 = 0.5 UMNW‐05 (D1) D1 F1DY7 MNW‐5‐D1‐17 4/18/2005 12:06 PDB GW µg/L 8.8 = 0.58 = 3.2 = 11 J 0.5 UMNW‐05 (D1) D1 F1DY6 MNW‐5‐D1‐12 4/18/2005 12:04 PDB GW µg/L 10 = 0.6 = 3.8 = 12 = 0.5 UMNW‐05 (D1) D1 F1DY4 MNW‐5‐D1‐7 4/18/2005 12:00 PDB GW µg/L 9.4 = 0.79 = 3.3 = 11 = 0.5 UMNW‐05 (D1) D1 F1DY3 MNW‐5‐D1‐2 4/18/2005 11:58 PDB GW µg/L 5.9 = 1.1 = 2.1 = 8.1 = 0.5 UMNW‐05 (D1) D1 F1D99 MNW‐5‐D1 4/18/2005 11:00 LFS GW µg/L 5.7 = 0.77 = 2.2 = 9.3 J 0.15 LJMNW‐05 (D1) D1 F17Q7 MNW‐5‐D1‐17 11/9/2004 11:00 PDB GW µg/L 7.5 = 0.3 LJv 3.2 = 10 Jv 0.21 LJMNW‐05 (D1) D1 F17Q5 MNW‐5‐D1‐7 11/9/2004 10:50 PDB GW µg/L 15 J^ 0.81 J 6 J^ 18 J 0.5 UJvMNW‐05 (D1) D1 F17Q4 MNW‐5‐D1‐2 11/9/2004 10:45 PDB GW µg/L 7.4 J 0.88 J 2.9 J 9.4 J 0.5 UJvMNW‐05 (D1) D1 MNW5D1Q403 MNW5D1Q403 11/24/2003 17:08 unknown GW µg/L 4.6 = 1.2 = 6.1 = 0.2227 <
MNW‐05 (D2) 5/10/2020 0:00 unknownMNW-05 (D2) D2 MNW-5-D2-7-0814 MNW-5-D2-7 8/25/2014 9:55 PDB GW ug/L 8.8 = 0.9 = 3.6 = 14.9 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐022014 MNW‐5‐D2‐7 2/18/2014 11:48 PDB GW µg/L 9.5 = 0.8 = 4.2 = 15.4 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐0813 MNW‐5‐D2‐7 8/13/2013 9:30 PDB GW µg/L 8.6 = 1 = 3.6 = 16.4 = 0.5 UMNW‐05 (D2) D2 F6PG1 MNW‐5‐D2‐7 2/13/2013 0:00 PDB GW µg/L 8 = 0.47 LJ 3.1 = 12 = 0.5 UMNW‐05 (D2) D2 F6CD9 MNW‐5‐D2‐7‐FD 8/20/2012 11:52 PDB GW µg/L 8.0 = 0.40 LJ 2.8 = 13 = 0.5 UMNW‐05 (D2) D2 F6CD8 MNW‐5‐D2‐7 8/20/2012 11:50 PDB GW µg/L 8.2 = 0.44 LJ 2.8 = 14 = 0.5 UMNW‐05 (D2) D2 F5G36 MNW‐5‐D2‐7 2/28/2012 11:09 PDB GW µg/L 5.5 = 0.28 LJ 2.3 = 9.1 = 0.5 UMNW‐05 (D2) D2 F4EC7 MNW‐5‐D2‐7‐Q311 8/22/2011 11:23 PDB GW µg/L 12 = 5.0 U 4.7 LJ 19 = 2.0 UMNW‐05 (D2) D2 MNW‐5‐D2‐5‐Q111 MNW‐5‐D2‐7 2/14/2011 9:17 PDB GW µg/L 5.3 = 0.5 U 1.7 = 8.6 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q310 MNW‐5‐D2‐7‐Q310 9/8/2010 12:45 PDB GW µg/L 7.2 = 0.5 = 2.5 = 10.5 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7_100201 MNW‐5‐D2‐7 2/1/2010 13:26 PDB GW µg/L 7 = 0.6 = 3.2 = 11.1 = 0.5 UMNW‐05 (D2) D2 F3B21 MNW‐5‐D2‐7 10/26/2009 14:52 PDB GW µg/L 8.2 = 0.67 = 3.4 = 13 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐FD‐Q209 MNW‐5‐D2‐7‐FD 4/20/2009 9:33 PDB GW µg/L 7.4 = 0.6 = 3.3 = 13.1 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q209 MNW‐5‐D2‐7 4/20/2009 9:32 PDB GW µg/L 7.0 = 0.6 = 3.2 = 12.9 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q408 MNW‐5‐D2‐7 10/7/2008 9:39 PDB GW µg/L 9.8 = 0.5 = 3.9 = 15.1 = 0.5 UMNW‐05 (D2) D2 F2RQ6 MNW‐5‐D2‐7 4/14/2008 0:00 PDB GW µg/L 8.9 = 0.81 = 3.5 = 14 = 0.5 UMNW‐05 (D2) D2 F2RQ8 MNW‐5‐D2‐12 4/14/2008 0:00 PDB GW µg/L 8.5 = 0.86 = 3.4 = 15 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q407 MNW‐5‐D2‐7 10/1/2007 11:25 PDB GW µg/L 10 = 0.6 = 4.3 = 17.3 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐12‐Q407 MNW‐5‐D2‐12 10/1/2007 11:20 PDB GW µg/L 8.2 = 0.7 = 3.4 = 14.6 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐12_070219 MNW‐5‐D2‐12 2/19/2007 9:39 PDB GW µg/L 7.5 JL 0.8 JL 3.3 JL 15.4 JL 0.5 UJMNW‐05 (D2) D2 MNW‐5‐D2‐7_070219 MNW‐5‐D2‐7 2/19/2007 9:32 PDB GW µg/L 9.5 JL 0.8 JL 4.2 JL 18.6 JL 0.5 UJMNW‐05 (D2) D2 F2680 MNW‐5‐D2‐12 8/28/2006 10:50 PDB GW µg/L 6.2 = 0.74 = 2.1 = 12 = 0.5 UMNW‐05 (D2) D2 F2681 MNW‐5‐D2‐7 8/28/2006 10:35 PDB GW µg/L 7.6 = 0.65 = 2.7 = 14 = 0.5 UMNW‐05 (D2) D2 F1YW0 MNW‐5‐D2‐12 2/6/2006 10:43 PDB GW µg/L 4.7 = 0.71 = 1.8 = 8.4 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 21 OF 72
011388
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐05 (D2) D2 F1YT8 MNW‐5‐D2‐7 2/6/2006 10:40 PDB GW µg/L 7.6 = 0.85 = 2.9 = 14 = 0.5 UMNW‐05 (D2) D2 F1P43 MNW‐5‐D2‐17 7/11/2005 13:31 PDB GW µg/L 5.2 = 0.78 = 1.8 = 7.9 = 0.12 LJMNW‐05 (D2) D2 F1P42 MNW‐5‐D2‐12 7/11/2005 13:28 PDB GW µg/L 6.4 = 0.77 = 2.3 = 9.4 = 0.11 LJMNW‐05 (D2) D2 F1P41 MNW‐5‐D2‐7 7/11/2005 13:27 PDB GW µg/L 9.2 = 0.92 = 3.5 = 14 = 0.15 LJMNW‐05 (D2) D2 F1P40 MNW‐5‐D2‐2 7/11/2005 13:25 PDB GW µg/L 9.3 = 0.98 = 3.6 = 15 = 0.5 UMNW‐05 (D2) D2 F1DZ1 MNW‐5‐D2‐17 4/18/2005 13:44 PDB GW µg/L 5.1 = 0.86 = 1.7 = 8.3 = 0.5 UMNW‐05 (D2) D2 F1DZ0 MNW‐5‐D2‐12 4/18/2005 13:42 PDB GW µg/L 7.3 = 1.3 = 2.6 = 12 = 0.5 UMNW‐05 (D2) D2 F1DY9 MNW‐5‐D2‐7 4/18/2005 13:40 PDB GW µg/L 8.7 = 0.91 = 2.8 = 13 = 0.5 UMNW‐05 (D2) D2 F1DY8 MNW‐5‐D2‐2 4/18/2005 13:38 PDB GW µg/L 9.2 = 1.4 = 3.4 = 15 = 0.5 UMNW‐05 (D2) D2 F17R1 MNW‐5‐D2‐17 11/9/2004 11:40 PDB GW µg/L 6.7 = 0.68 = 2.3 = 12 = 0.5 UMNW‐05 (D2) D2 F17Q9 MNW‐5‐D2‐7 11/9/2004 11:30 PDB GW µg/L 12 = 1.2 = 3.9 = 22 = 0.5 UMNW‐05 (D2) D2 F17Q8 MNW‐5‐D2‐2 11/9/2004 11:25 PDB GW µg/L 10 J^ 0.25 LJ 3.2 J^ 10 J 0.35 LJMNW‐05 (D2) D2 MNW5D2Q403 MNW5D2Q403 12/11/2003 11:43 unknown GW µg/L 4.3 = 0.9 J 6.8 = 0.2227 <
MNW‐05 (D3) 5/10/2020 0:00 unknownMNW-05 (D3) D3 MNW-5-D3-17-0814-FD MNW-5-D3-17 8/25/2014 9:30 PDB GW ug/L 9.8 = 0.5 U 6.4 = 16.2 = 0.5 UMNW-05 (D3) D3 MNW-5-D3-17-0814 MNW-5-D3-17 8/25/2014 9:28 PDB GW ug/L 9.9 = 0.5 U 6.1 = 16.4 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐022014 MNW‐5‐D3‐17 2/18/2014 11:30 PDB GW µg/L 9 = 0.5 U 4.8 = 16.1 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐0813 MNW‐5‐D3‐17 8/13/2013 9:40 PDB GW µg/L 8.2 = 0.9 = 3.8 = 19 = 0.5 UMNW‐05 (D3) D3 F6PG2 MNW‐5‐D3‐17 2/13/2013 0:00 PDB GW µg/L 8.7 = 0.74 = 3.3 = 16 = 0.5 UMNW‐05 (D3) D3 F6CE0 MNW‐5‐D3‐17 8/20/2012 11:35 PDB GW µg/L 10 = 0.74 = 3.0 = 22 = 0.5 UMNW‐05 (D3) D3 F5G37 MNW‐5‐D3‐17 2/28/2012 11:30 PDB GW µg/L 6.9 = 0.42 LJ 2.6 = 15 = 0.5 UMNW‐05 (D3) D3 F4EC8 MNW‐5‐D3‐17‐Q311 8/22/2011 11:25 PDB GW µg/L 13 = 5.0 U 4.9 LJ 27 = 2.0 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q111 MNW‐5‐D3‐17 2/14/2011 9:29 PDB GW µg/L 8.8 = 0.5 U 2.9 = 18.2 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q310 MNW‐5‐D3‐17‐Q310 9/8/2010 13:35 PDB GW µg/L 9.5 = 0.5 U 4.2 = 17.3 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17_100201 MNW‐5‐D3‐17 2/1/2010 12:49 PDB GW µg/L 10.6 = 0.5 U 6.2 = 15.8 = 0.5 UMNW‐05 (D3) D3 F3B22 MNW‐5‐D3‐17 10/26/2009 15:05 PDB GW µg/L 9.4 = 0.41 LJ 4.2 = 16 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q209 MNW‐5‐D3‐17 4/20/2009 9:48 PDB GW µg/L 9.1 J 0.5 J 3.7 J 17.8 J 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q408 MNW‐5‐D3‐17 10/7/2008 9:23 PDB GW µg/L 9.4 = 0.8 = 3.5 = 19.2 = 0.5 UMNW‐05 (D3) D3 F2RQ9 MNW‐5‐D3‐17 4/14/2008 0:00 PDB GW µg/L 14 = 1 = 4.7 = 18 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q407 MNW‐5‐D3‐17 10/1/2007 10:55 PDB GW µg/L 10.8 = 0.9 = 3.9 = 19.6 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3_070219 MNW‐5‐D3‐17 2/19/2007 10:00 PDB GW µg/L 10.4 JL 1 JL 3.4 JL 19.5 JL 0.5 UJMNW‐05 (D3) D3 F2683 MNW‐5‐D3‐17 8/28/2006 11:10 PDB GW µg/L 8.3 = 0.89 = 2.1 = 16 = 0.5 UMNW‐05 (D3) D3 F1YW2 MNW‐5‐D3‐17 2/6/2006 10:50 PDB GW µg/L 6 = 0.93 = 1.6 = 11 = 0.5 UMNW‐05 (D3) D3 F1YW1 MNW‐5‐D3‐12 2/6/2006 10:43 PDB GW µg/L 2.1 = 0.5 U 0.59 = 3.8 = 0.5 UMNW‐05 (D3) D3 F1P48 MNW‐5‐D3‐17 7/11/2005 13:49 PDB GW µg/L 6.9 = 0.86 = 1.6 = 11 = 0.5 UMNW‐05 (D3) D3 F1P47 MNW‐5‐D3‐12 7/11/2005 13:47 PDB GW µg/L 2.4 = 0.69 = 1.1 = 8.5 J 0.5 UMNW‐05 (D3) D3 F1P44 MNW‐5‐D3‐2 7/11/2005 13:40 PDB GW µg/L 1.7 = 0.25 LJ 0.46 LJ 3.1 = 0.5 UMNW‐05 (D3) D3 F1P45 MNW‐5‐D3‐7 7/11/2005 13:33 PDB GW µg/L 2.2 = 0.35 LJ 0.56 = 3.8 = 0.5 UMNW‐05 (D3) D3 F1DZ6 MNW‐5‐D3‐17 4/18/2005 14:08 PDB GW µg/L 6.7 = 1.3 = 1.7 = 13 = 0.5 UMNW‐05 (D3) D3 F1DZ5 MNW‐5‐D3‐12 4/18/2005 14:06 PDB GW µg/L 2.8 = 0.77 = 0.65 = 5.7 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 22 OF 72
011389
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐05 (D3) D3 F1DZ3 MNW‐5‐D3‐7 4/18/2005 14:02 PDB GW µg/L 2 = 0.48 LJ 0.49 LJ 4.0 = 0.5 UMNW‐05 (D3) D3 F1DZ2 MNW‐5‐D3‐2 4/18/2005 14:00 PDB GW µg/L 2.2 = 0.47 LJ 0.55 = 4.0 = 0.5 UMNW‐05 (D3) D3 F17R6 MNW‐5‐D3‐17 11/9/2004 11:25 PDB GW µg/L 4.9 = 0.68 = 1.1 = 10 = 0.5 UMNW‐05 (D3) D3 F17R5 MNW‐5‐D3‐12 11/9/2004 11:15 PDB GW µg/L 1.8 = 0.24 LJ 0.49 LJ 3.9 = 0.5 UMNW‐05 (D3) D3 F17R3 MNW‐5‐D3‐7 11/9/2004 11:10 PDB GW µg/L 2.1 = 0.24 LJ 0.53 = 4.3 = 0.5 UMNW‐05 (D3) D3 F17R2 MNW‐5‐D3‐2 11/9/2004 11:05 PDB GW µg/L 2 = 0.22 LJ 0.42 LJ 4.0 = 0.5 UMNW‐05 (D3) D3 MNW5D3Q403 MNW5D3Q403 12/10/2003 16:03 unknown GW µg/L 3.7 = 0.7936 < 7.1 = 0.2227 <
MNW‐05 (D4) 5/10/2020 0:00 unknownMNW‐05 (D4) D4 MNW‐5‐D4‐7‐022014 MNW‐5‐D4‐7 2/18/2014 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F6PG4 MNW‐5‐D4‐7‐FD 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F6PG3 MNW‐5‐D4‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJvMNW‐05 (D4) D4 F5G39 MNW‐5‐D4‐7‐FD 2/28/2012 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F5G38 MNW‐5‐D4‐7 2/28/2012 9:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐5‐Q111 MNW‐5‐D4‐7 2/14/2011 9:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7_100201 MNW‐5‐D4‐7 2/1/2010 12:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7‐Q209 MNW‐5‐D4‐7 4/20/2009 9:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7‐Q408 MNW‐5‐D4‐7 10/7/2008 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F2RR0 MNW‐5‐D4‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7‐Q407 MNW‐5‐D4‐7 10/1/2007 11:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4_070219 MNW‐5‐D4‐7 2/19/2007 10:17 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐05 (D4) D4 F2684 MNW‐5‐D4‐7 8/28/2006 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1YW3 MNW‐5‐D4‐7 2/6/2006 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P52 MNW‐5‐D4‐17 7/11/2005 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P51 MNW‐5‐D4‐12 7/11/2005 14:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P50 MNW‐5‐D4‐7 7/11/2005 14:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P49 MNW‐5‐D4‐2 7/11/2005 14:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1E00 MNW‐5‐D4‐17 4/18/2005 14:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1DZ9 MNW‐5‐D4‐12 4/18/2005 14:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1DZ8 MNW‐5‐D4‐7 4/18/2005 14:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1DZ7 MNW‐5‐D4‐2 4/18/2005 14:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐06 (D1) 5/10/2020 0:00 unknownMNW‐06 (D1) D1 F6PG6 MNW‐6‐D1‐7‐FD 2/13/2013 0:00 PDB GW µg/L 0.52 = 0.5 U 0.5 U 2.1 = 0.5 UMNW‐06 (D1) D1 F6PG5 MNW‐6‐D1‐7 2/13/2013 0:00 PDB GW µg/L 0.62 = 0.5 U 0.16 LJ 2.4 = 0.5 UJvMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q111‐FD MNW‐6‐D1‐7 2/14/2011 9:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1 = 0.5 UMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q111 MNW‐6‐D1‐7 2/14/2011 8:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1 = 0.5 UMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q209 MNW‐6‐D1‐7 4/20/2009 7:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q407 MNW‐6‐D1‐7 10/2/2007 11:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F1P56 MNW‐6‐D1‐17 7/12/2005 8:15 PDB GW µg/L 0.5 U 0.076 LJ 0.5 U 0.13 LJ 0.5 UMNW‐06 (D1) D1 F1P55 MNW‐6‐D1‐12 7/12/2005 8:14 PDB GW µg/L 0.086 LJ 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐06 (D1) D1 F1P54 MNW‐6‐D1‐7 7/12/2005 8:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.11 LJ 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 23 OF 72
011390
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐06 (D1) D1 F1P53 MNW‐6‐D1‐2 7/12/2005 8:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.1 LJ 0.5 UMNW‐06 (D1) D1 F1E04 MNW‐6‐D1‐17 4/19/2005 14:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UMNW‐06 (D1) D1 F1E03 MNW‐6‐D1‐12 4/19/2005 14:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.18 LJ 0.5 UMNW‐06 (D1) D1 F1E02 MNW‐6‐D1‐7 4/19/2005 14:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.22 LJ 0.5 UMNW‐06 (D1) D1 F1E01 MNW‐6‐D1‐2 4/19/2005 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UMNW‐06 (D1) D1 F17S0 MNW‐6‐D1‐17 11/10/2004 8:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F17R9 MNW‐6‐D1‐12 11/10/2004 8:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F17R8 MNW‐6‐D1‐7 11/10/2004 8:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F17R7 MNW‐6‐D1‐2 11/10/2004 8:10 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐06 (D1) D1 MNW6D1Q403 MNW6D1Q403 11/14/2003 15:44 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐06 (D2) 5/10/2020 0:00 unknownMNW‐06 (D2) D2 F6PG7 MNW‐6‐D2‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJvMNW‐06 (D2) D2 MNW‐6‐D2‐7‐Q111 MNW‐6‐D2‐7 2/14/2011 8:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 MNW‐6‐D2‐7‐Q209 MNW‐6‐D2‐7 4/20/2009 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 MNW‐6‐D2‐7‐Q407 MNW‐6‐D2‐7 10/2/2007 11:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F1P60 MNW‐6‐D2‐17 7/12/2005 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.091 LJ 0.5 UMNW‐06 (D2) D2 F1P59 MNW‐6‐D2‐12 7/12/2005 8:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 UMNW‐06 (D2) D2 F1P58 MNW‐6‐D2‐7 7/12/2005 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐06 (D2) D2 F1P57 MNW‐6‐D2‐2 7/12/2005 8:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐06 (D2) D2 F1E08 MNW‐6‐D2‐17 4/19/2005 14:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F1E07 MNW‐6‐D2‐12 4/19/2005 14:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F1E06 MNW‐6‐D2‐7 4/19/2005 14:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐06 (D2) D2 F1E05 MNW‐6‐D2‐2 4/19/2005 14:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐06 (D2) D2 F17D6 MNW‐6‐D2 11/9/2004 11:40 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UMNW‐06 (D2) D2 F17S4 MNW‐6‐D2‐17 11/9/2004 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F17S3 MNW‐6‐D2‐12 11/9/2004 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F17S2 MNW‐6‐D2‐7 11/9/2004 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 MNW6D2Q403 MNW6D2Q403 11/17/2003 10:08 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.3 J
MNW‐06 (D3) 5/10/2020 0:00 unknownMNW‐06 (D3) D3 MNW‐6‐D3‐7‐022014 MNW‐6‐D3‐7 2/17/2014 12:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F6PG8 MNW‐6‐D3‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F5G40 MNW‐6‐D3‐7 2/28/2012 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7‐Q111 MNW‐6‐D3‐7 2/14/2011 8:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7_100201 MNW‐6‐D3‐7 2/1/2010 13:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7‐Q209 MNW‐6‐D3‐7 4/20/2009 8:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7‐Q407 MNW‐6‐D3‐7 10/2/2007 11:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1P64 MNW‐6‐D3‐17 7/12/2005 9:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1P63 MNW‐6‐D3‐12 7/12/2005 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1P62 MNW‐6‐D3‐7 7/12/2005 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1P61 MNW‐6‐D3‐2 7/12/2005 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.084 LJMNW‐06 (D3) D3 F1E12 MNW‐6‐D3‐17 4/19/2005 15:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1E11 MNW‐6‐D3‐12 4/19/2005 15:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 24 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐06 (D3) D3 F1E10 MNW‐6‐D3‐7 4/19/2005 15:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1E09 MNW‐6‐D3‐2 4/19/2005 15:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S8 MNW‐6‐D3‐17 11/10/2004 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S7 MNW‐6‐D3‐12 11/10/2004 8:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S6 MNW‐6‐D3‐7 11/10/2004 7:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S5 MNW‐6‐D3‐2 11/10/2004 7:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW6D3Q403 MNW6D3Q403 11/17/2003 15:16 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.3 J
MNW‐07 (D4) 5/10/2020 0:00 unknownMNW‐07 (D4) D4 F6PG9 MNW‐7‐D4‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F3S26 MNW‐7‐D4‐7 2/15/2011 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4‐7‐Q209 MNW‐7‐D4‐7 4/20/2009 12:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4‐7‐Q408 MNW‐7‐D4‐7 10/7/2008 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F2RR1 MNW‐7‐D4‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4‐7‐Q407 MNW‐7‐D4‐7 10/2/2007 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4_070219 MNW‐7‐D4‐7 2/19/2007 10:54 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐07 (D4) D4 F2685 MNW‐7‐D4‐7 8/28/2006 14:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P96 MNW‐7‐D4‐17 7/12/2005 12:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P95 MNW‐7‐D4‐12 7/12/2005 12:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P94 MNW‐7‐D4‐7 7/12/2005 12:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P92 MNW‐7‐D4‐2 7/12/2005 12:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E44 MNW‐7‐D4‐17 4/18/2005 15:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E43 MNW‐7‐D4‐12 4/18/2005 15:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E40 MNW‐7‐D4‐2 4/18/2005 15:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E42 MNW‐7‐D4‐7 4/18/2005 14:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17T3 MNW‐7‐D4‐17 11/10/2004 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17T2 MNW‐7‐D4‐12 11/10/2004 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17T1 MNW‐7‐D4‐7 11/10/2004 8:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17S9 MNW‐7‐D4‐2 11/10/2004 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW7Q403 MNW7Q403 11/22/2003 17:00 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐08 (I1) 5/10/2020 0:00 unknownMNW‐08 (I1) I1 F6PH0 MNW‐8‐I1‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F6PH1 MNW‐8‐I1‐7‐FD 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 MNW‐8‐I1‐7‐Q111 MNW‐8‐I1‐7 2/16/2011 13:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1NG3 MNW‐8‐I1‐12 7/12/2005 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1NG2 MNW‐8‐I1‐7 7/12/2005 8:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1NG1 MNW‐8‐I1‐2 7/12/2005 8:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1DC4 MNW‐8‐I1‐12 4/20/2005 9:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1DC3 MNW‐8‐I1‐7 4/20/2005 9:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1DC2 MNW‐8‐I1‐2 4/20/2005 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F17J3 MNW‐8‐I1‐12 11/9/2004 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F17J2 MNW‐8‐I1‐7 11/9/2004 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 25 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐08 (I1) I1 F17J1 MNW‐8‐I1‐2 11/9/2004 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 MNW8I1Q403 MNW8I1Q403 12/14/2003 14:45 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐08 (I2) 5/10/2020 0:00 unknownMNW-08 (I2) I2 MNW-8-I2-7-0814 MNW-8-I2-7 8/25/2014 8:04 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐022014 MNW‐8‐I2‐7 2/17/2014 8:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐0813 MNW‐8‐I2‐7 8/13/2013 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F6PH2 MNW‐8‐I2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F6CA4 MNW‐8‐I2‐7 8/20/2012 9:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F5G41 MNW‐8‐I2‐7 2/28/2012 8:00 PDB GW µg/L 4.7 = 0.61 = 2 = 11 = 0.5 UMNW‐08 (I2) I2 F4EC9 MNW‐8‐I2‐7‐Q311 8/23/2011 7:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q111 MNW‐8‐I2‐7 2/16/2011 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q310 MNW‐8‐I2‐7‐Q310 9/8/2010 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7_100201 MNW‐8‐I2‐7 2/1/2010 10:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F3B36 MNW‐8‐I2‐7 10/26/2009 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q209 MNW‐8‐I2‐7 4/21/2009 7:36 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q407 MNW‐8‐I2‐7 10/2/2007 8:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG7 MNW‐8‐I2‐17 7/12/2005 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG6 MNW‐8‐I2‐12 7/12/2005 8:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG5 MNW‐8‐I2‐7 7/12/2005 8:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG4 MNW‐8‐I2‐2 7/12/2005 8:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC8 MNW‐8‐I2‐17 4/20/2005 9:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC7 MNW‐8‐I2‐12 4/20/2005 9:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC6 MNW‐8‐I2‐7 4/20/2005 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC5 MNW‐8‐I2‐2 4/20/2005 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17D7 MNW‐8‐I2 11/16/2004 8:50 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.44 LJ 0.5 UMNW‐08 (I2) I2 F17J7 MNW‐8‐I2‐17 11/9/2004 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17J6 MNW‐8‐I2‐12 11/9/2004 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17J5 MNW‐8‐I2‐7 11/9/2004 10:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17J4 MNW‐8‐I2‐2 11/9/2004 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW8I2Q403 MNW8I2Q403 12/14/2003 11:26 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐09 (D1) 5/10/2020 0:00 unknownMNW-09 (D1) D1 MNW-9-D1-2-0814-FD MNW-9-D1-2 8/25/2014 13:47 PDB GW ug/L 1.4 = 0.5 U 1.6 = 2.5 = 0.5 UMNW-09 (D1) D1 MNW-9-D1-2-0814 MNW-9-D1-2 8/25/2014 12:47 PDB GW ug/L 1.3 = 0.5 U 1.0 = 3.6 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐022014 MNW‐9‐D1‐2 2/17/2014 10:15 PDB GW µg/L 1 = 0.5 U 0.6 = 3.1 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐0813 MNW‐9‐D1‐2 8/13/2013 9:58 PDB GW µg/L 1.3 = 0.5 U 1.9 = 3.1 = 0.5 UMNW‐09 (D1) D1 F6PH3 MNW‐9‐D1‐2 2/18/2013 0:00 PDB GW µg/L 0.83 = 0.5 U 0.56 = 2.9 = 0.5 UMNW‐09 (D1) D1 F6CE1 MNW‐9‐D1‐2 8/20/2012 13:49 PDB GW µg/L 0.92 = 0.048 LJ 0.53 = 4.6 J^ 0.5 UMNW‐09 (D1) D1 F5G42 MNW‐9‐D1‐2 2/27/2012 12:57 PDB GW µg/L 0.57 = 0.5 U 0.29 LJ 2.3 = 0.5 UMNW‐09 (D1) D1 F4ED1 MNW‐9‐D1‐2‐Q311 8/22/2011 9:25 PDB GW µg/L 1.7 LJ 5.0 U 1.6 LJ 5.7 = 2.0 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q111 MNW‐9‐D1‐2 2/16/2011 11:28 PDB GW µg/L 0.7 = 0.5 U 0.5 U 3.4 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 26 OF 72
011393
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐09 (D1) D1 F3LQ7 MNW‐9‐D1‐2‐Q310‐FD 9/2/2010 14:10 PDB GW µg/L 0.96 = 0.5 U 0.39 LJ 4.4 = 0.5 UMNW‐09 (D1) D1 F3LQ6 MNW‐9‐D1‐2‐Q310 9/2/2010 13:10 PDB GW µg/L 1 = 0.5 U 0.42 LJ 4.8 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2_100202‐FD MNW‐9‐D1‐2 2/2/2010 11:30 PDB GW µg/L 0.8 = 0.5 U 0.6 = 3.3 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2_100202 MNW‐9‐D1‐2 2/2/2010 10:30 PDB GW µg/L 0.8 = 0.5 U 0.6 = 3.4 = 0.5 UMNW‐09 (D1) D1 F3B24 MNW‐9‐D1‐2 10/26/2009 8:45 PDB GW µg/L 1.2 = 0.5 U 0.62 = 5.2 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐FD‐Q209 MNW‐9‐D1‐2‐FD 4/20/2009 14:00 PDB GW µg/L 1.3 J 0.5 U 0.6 J 5.0 J 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q209 MNW‐9‐D1‐2 4/20/2009 13:53 PDB GW µg/L 1.2 J 0.5 U 0.7 J 5.2 J 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q408 MNW‐9‐D1‐2 10/6/2008 10:15 PDB GW µg/L 5.1 = 0.5 U 7.2 = 2.2 = 0.5 UMNW‐09 (D1) D1 F2RR4 MNW‐9‐D1‐2 4/14/2008 0:00 PDB GW µg/L 2.3 = 0.5 U 2.1 = 5.6 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q407 MNW‐9‐D1‐2 10/1/2007 11:31 PDB GW µg/L 3.8 = 0.5 U 4 = 8.8 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐070222 MNW‐9‐D1‐2 2/22/2007 11:00 PDB GW µg/L 0.8 = 0.5 U 0.5 U 4.6 = 0.5 UMNW‐09 (D1) D1 F2686 MNW‐9‐D1‐2 8/29/2006 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 3.4 = 0.5 UMNW‐09 (D1) D1 F1YM3 MNW‐9‐D1‐17 2/6/2006 10:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.9 = 0.5 UMNW‐09 (D1) D1 F1YM2 MNW‐9‐D1‐12 2/6/2006 10:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2 = 0.5 UMNW‐09 (D1) D1 F1YM0 MNW‐9‐D1‐7 2/6/2006 10:38 PDB GW µg/L 0.51 = 0.5 U 0.5 U 3.2 = 0.5 UMNW‐09 (D1) D1 F1YL9 MNW‐9‐D1‐2 2/6/2006 10:37 PDB GW µg/L 0.69 = 0.5 U 0.5 U 4.2 = 0.5 UMNW‐09 (D1) D1 F1NJ0 MNW‐9‐D1‐17 7/11/2005 14:11 PDB GW µg/L 1.1 = 0.5 U 0.5 U 5.3 = 0.11 LJMNW‐09 (D1) D1 F1NH9 MNW‐9‐D1‐12 7/11/2005 14:09 PDB GW µg/L 1.7 = 0.5 U 0.5 U 8 = 0.5 UMNW‐09 (D1) D1 F1NH8 MNW‐9‐D1‐7 7/11/2005 14:07 PDB GW µg/L 1.2 = 0.5 U 0.5 U 6.2 = 0.5 UMNW‐09 (D1) D1 F1NH7 MNW‐9‐D1‐2 7/11/2005 14:05 PDB GW µg/L 3.4 = 0.5 U 0.13 LJ 15 = 0.5 UMNW‐09 (D1) D1 F1DA3 MNW‐9‐D1 4/20/2005 12:05 LFS GW µg/L 0.35 LJ 0.5 U 0.5 U 2.9 = 0.5 UMNW‐09 (D1) D1 F1DE1 MNW‐9‐D1‐17 4/19/2005 14:34 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 1.3 = 0.5 UMNW‐09 (D1) D1 F1DE0 MNW‐9‐D1‐12 4/19/2005 14:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 UMNW‐09 (D1) D1 F1DD9 MNW‐9‐D1‐7 4/19/2005 14:28 PDB GW µg/L 0.34 LJ 0.5 U 0.5 U 1.5 = 0.5 UMNW‐09 (D1) D1 F1DD8 MNW‐9‐D1‐2 4/19/2005 14:24 PDB GW µg/L 0.4 LJ 0.5 U 0.5 U 2.2 = 0.5 U
MNW‐09 (D2) 5/10/2020 0:00 unknownMNW‐09 (D2) D2 F6PH4 MNW‐9‐D2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q111 MNW‐9‐D2‐7 2/16/2011 11:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q209 MNW‐9‐D2‐7 4/20/2009 13:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q408 MNW‐9‐D2‐7 10/6/2008 10:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F2RR6 MNW‐9‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q407 MNW‐9‐D2‐7 10/1/2007 11:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐070222 MNW‐9‐D2‐7 2/22/2007 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F2688 MNW‐9‐D2‐7 8/29/2006 11:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1YM4 MNW‐9‐D2‐2 2/6/2006 10:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ4 MNW‐9‐D2‐17 7/11/2005 14:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ3 MNW‐9‐D2‐12 7/11/2005 14:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ2 MNW‐9‐D2‐7 7/11/2005 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ1 MNW‐9‐D2‐2 7/11/2005 14:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1DE5 MNW‐9‐D2‐17 4/19/2005 14:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 27 OF 72
011394
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐09 (D2) D2 F1DE4 MNW‐9‐D2‐12 4/19/2005 14:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1DE3 MNW‐9‐D2‐7 4/19/2005 14:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1DE2 MNW‐9‐D2‐2 4/19/2005 14:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐09 (I1) 5/10/2020 0:00 unknownMNW‐09 (I1) I1 F6PH5 MNW‐9‐I1‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐7‐Q111 MNW‐9‐I1‐7 2/16/2011 11:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐7‐Q209 MNW‐9‐I1‐7 4/20/2009 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐7‐Q408 MNW‐9‐I1‐7 10/6/2008 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F2RR2 MNW‐9‐I1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐7‐Q407 MNW‐9‐I1‐7 10/1/2007 12:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1_070219 MNW‐9‐I1‐7 2/19/2007 12:53 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐09 (I1) I1 F2689 MNW‐9‐I1‐7 8/29/2006 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1YL7 MNW‐9‐I1‐7 2/6/2006 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1NH0 MNW‐9‐I1‐12 7/11/2005 13:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1NG9 MNW‐9‐I1‐7 7/11/2005 13:26 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐09 (I1) I1 F1NG8 MNW‐9‐I1‐2 7/11/2005 13:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.12 LJMNW‐09 (I1) I1 F1DD1 MNW‐9‐I1‐12 4/19/2005 13:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1DD0 MNW‐9‐I1‐7 4/19/2005 13:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1DC9 MNW‐9‐I1‐2 4/19/2005 13:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F17K0 MNW‐9‐I1‐12 11/8/2004 12:41 PDB GW µg/L 0.5 UJv 0.5 UJv 0.5 UJv 0.5 UJv 0.5 UJvMNW‐09 (I1) I1 F17J9 MNW‐9‐I1‐7 11/8/2004 12:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F17J8 MNW‐9‐I1‐2 11/8/2004 12:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW9I1Q403 MNW9I1Q403 12/17/2003 14:55 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐09 (I2) 5/10/2020 0:00 unknownMNW-09 (I2) I2 MNW-9-I2-17-0814 MNW-9-I2-17 8/25/2014 12:37 PDB GW ug/L 1.4 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐022014 MNW‐9‐I2‐17 2/17/2014 10:07 PDB GW µg/L 1.3 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐0813 MNW‐9‐I2‐17 8/13/2013 10:07 PDB GW µg/L 1.3 = 0.5 U 0.6 = 3.8 = 0.5 UMNW‐09 (I2) I2 F6PH6 MNW‐9‐I2‐17 2/18/2013 0:00 PDB GW µg/L 1.6 = 0.5 U 0.37 LJ 3.6 = 0.5 UMNW‐09 (I2) I2 F6CE2 MNW‐9‐I2‐17 8/20/2012 13:46 PDB GW µg/L 1.6 = 0.032 LJ 0.25 LJ 5.4 J^ 0.5 UMNW‐09 (I2) I2 F5G43 MNW‐9‐I2‐17 2/27/2012 12:47 PDB GW µg/L 1.5 = 0.5 U 0.5 U 4.5 = 0.5 UMNW‐09 (I2) I2 F4ED0 MNW‐9‐12‐17‐FD‐Q311 8/22/2011 9:18 PDB GW µg/L 2.7 LJ 5.0 U 5.0 U 9.2 = 2.0 UMNW‐09 (I2) I2 F4ED2 MNW‐9‐I2‐17‐Q311 8/22/2011 9:17 PDB GW µg/L 2.6 LJ 5.0 U 5.0 U 8.9 = 2.0 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q111 MNW‐9‐I2‐17 2/16/2011 11:38 PDB GW µg/L 1.9 = 0.5 U 0.5 U 7.2 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q310 MNW‐9‐I2‐17‐Q310 9/7/2010 8:37 PDB GW µg/L 2.9 = 0.5 U 0.5 U 9.4 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17_100202 MNW‐9‐I2‐17 2/2/2010 10:40 PDB GW µg/L 2.9 = 0.5 U 0.5 U 12.1 = 0.5 UMNW‐09 (I2) I2 F3B23 MNW‐9‐I2‐17 10/26/2009 8:38 PDB GW µg/L 2.7 = 0.5 U 0.5 U 11 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q209 MNW‐9‐I2‐17 4/20/2009 14:16 PDB GW µg/L 3.2 J 0.5 U 0.5 U 13.8 J 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q408 MNW‐9‐I2‐17 10/6/2008 10:39 PDB GW µg/L 4.4 = 0.5 U 0.5 U 16.2 = 0.5 UMNW‐09 (I2) I2 F2RR3 MNW‐9‐I2‐17 4/14/2008 0:00 PDB GW µg/L 4.9 = 0.5 U 0.14 LJ 19 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q407 MNW‐9‐I2‐17 10/1/2007 11:53 PDB GW µg/L 4.1 = 0.5 U 0.5 U 16.4 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 28 OF 72
011395
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐09 (I2) I2 MNW‐9‐I2_070219 MNW‐9‐I2‐17 2/19/2007 13:00 PDB GW µg/L 3.6 JL 0.5 UJ 0.5 UJ 18.8 JL 0.5 UJMNW‐09 (I2) I2 F2690 MNW‐9‐I2‐17 8/29/2006 11:00 PDB GW µg/L 2.5 = 0.5 U 0.5 U 17 = 0.5 UMNW‐09 (I2) I2 F1YL8 MNW‐9‐I2‐17 2/6/2006 10:26 PDB GW µg/L 3.6 = 0.5 U 0.5 U 20 = 0.5 UMNW‐09 (I2) I2 F1NH6 MNW‐9‐I2‐17 7/11/2005 13:49 PDB GW µg/L 4.9 = 0.5 U 0.18 LJ 21 = 0.14 LJMNW‐09 (I2) I2 F1NH5 MNW‐9‐I2‐12 7/11/2005 13:42 PDB GW µg/L 4.7 = 0.5 U 0.17 LJ 21 J 0.5 UMNW‐09 (I2) I2 F1NH3 MNW‐9‐I2‐7 7/11/2005 13:39 PDB GW µg/L 3.4 = 0.5 U 0.12 LJ 16 = 0.13 LJMNW‐09 (I2) I2 F1NH2 MNW‐9‐I2‐2 7/11/2005 13:37 PDB GW µg/L 3.3 = 0.5 U 0.12 LJ 18 = 0.16 LJMNW‐09 (I2) I2 F1DA1 MNW‐9‐I2 4/20/2005 9:20 LFS GW µg/L 2.6 = 0.5 U 0.5 U 14 J 0.5 UMNW‐09 (I2) I2 F1DD7 MNW‐9‐I2‐17 4/19/2005 13:54 PDB GW µg/L 4.3 = 0.5 U 0.5 U 22 = 0.5 UMNW‐09 (I2) I2 F1DD6 MNW‐9‐I2‐12 4/19/2005 13:50 PDB GW µg/L 3.6 = 0.5 U 0.11 LJ 18 J 0.5 UMNW‐09 (I2) I2 F1DD4 MNW‐9‐I2‐7 4/19/2005 13:44 PDB GW µg/L 3.5 = 0.5 U 0.11 LJ 18 = 0.5 UMNW‐09 (I2) I2 F1DD3 MNW‐9‐I2‐2 4/19/2005 13:40 PDB GW µg/L 3.3 = 0.5 U 0.11 LJ 16 = 0.5 UMNW‐09 (I2) I2 F17K6 MNW‐9‐I2‐17 11/8/2004 13:35 PDB GW µg/L 3.9 = 0.5 U 0.5 U 19 = 0.5 UMNW‐09 (I2) I2 F17K5 MNW‐9‐I2‐12 11/8/2004 13:25 PDB GW µg/L 3.9 = 0.5 U 0.5 U 19 = 0.5 UMNW‐09 (I2) I2 F17K3 MNW‐9‐I2‐7 11/8/2004 13:15 PDB GW µg/L 3.8 = 0.5 U 0.5 U 17 = 0.5 UMNW‐09 (I2) I2 F17K2 MNW‐9‐I2‐2 11/8/2004 13:00 PDB GW µg/L 3.3 = 0.5 U 0.5 U 7.9 = 0.37 LJMNW‐09 (I2) I2 MNW9I2Q403 MNW9I2Q403 12/18/2003 17:05 unknown GW µg/L 2.2 = 0.7936 < 11 = 0.2227 <
MNW‐10 (I1) 5/10/2020 0:00 unknownMNW‐10 (I1) I1 MNW‐10‐I1‐2‐Q209 MNW‐10‐I1‐2 4/20/2009 10:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 MNW‐10‐I1‐2‐Q408 MNW‐10‐I1‐2 10/6/2008 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F2RR7 MNW‐10‐I1‐2 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 MNW‐10‐I1‐2‐Q407 MNW‐10‐I1‐2 10/1/2007 11:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 MNW‐10‐I1_070219 MNW‐10‐I1‐2 2/19/2007 13:36 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐10 (I1) I1 F2644 MNW‐10‐I1‐2 8/28/2006 12:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1YM5 MNW‐10‐I1‐2 2/6/2006 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1NJ7 MNW‐10‐I1‐12 7/12/2005 8:48 PDB GW µg/L 0.34 LJv 0.5 U 0.084 LJv 0.067 LJ 0.5 UMNW‐10 (I1) I1 F1NJ6 MNW‐10‐I1‐7 7/12/2005 8:47 PDB GW µg/L 0.31 LJ 0.5 U 0.5 U 0.076 LJ 0.5 UMNW‐10 (I1) I1 F1NJ5 MNW‐10‐I1‐2 7/12/2005 8:46 PDB GW µg/L 0.44 LJ 0.5 U 0.12 LJ 0.082 LJ 0.056 LJMNW‐10 (I1) I1 F1DE8 MNW‐10‐I1‐12 4/20/2005 10:36 PDB GW µg/L 0.33 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1DE7 MNW‐10‐I1‐7 4/20/2005 10:33 PDB GW µg/L 0.35 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1DE6 MNW‐10‐I1‐2 4/20/2005 10:30 PDB GW µg/L 0.35 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F17H2 MNW‐10‐I1‐12 11/8/2004 10:10 PDB GW µg/L 0.25 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F17H1 MNW‐10‐I1‐7 11/8/2004 10:03 PDB GW µg/L 0.31 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F17H0 MNW‐10‐I1‐2 11/8/2004 9:57 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 MNW10I1Q403 MNW10I1Q403 12/20/2003 10:43 unknown GW µg/L 0.4 J 0.7936 < 0.3733 < 0.2227 <
MNW‐10 (I2) 5/10/2020 0:00 unknownMNW‐10 (I2) I2 F6PB3 MNW‐10‐I2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F3S44 MNW‐10‐I2‐7 2/15/2011 10:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2‐7‐Q209 MNW‐10‐I2‐7 4/20/2009 11:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2‐7‐Q408 MNW‐10‐I2‐7 10/6/2008 11:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 29 OF 72
011396
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐10 (I2) I2 F2RR8 MNW‐10‐I2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2‐7‐Q407 MNW‐10‐I2‐7 10/1/2007 11:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2_070219 MNW‐10‐I2‐7 2/19/2007 13:45 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐10 (I2) I2 F2645 MNW‐10‐I2‐7 8/28/2006 12:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1YM6 MNW‐10‐I2‐7 2/6/2006 9:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NK1 MNW‐10‐I2‐17 7/12/2005 8:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NK0 MNW‐10‐I2‐12 7/12/2005 8:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NJ9 MNW‐10‐I2‐7 7/12/2005 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NJ8 MNW‐10‐I2‐2 7/12/2005 8:55 PDB GW µg/L 0.17 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DF2 MNW‐10‐I2‐17 4/20/2005 10:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DF1 MNW‐10‐I2‐12 4/20/2005 10:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DF0 MNW‐10‐I2‐7 4/20/2005 10:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DE9 MNW‐10‐I2‐2 4/20/2005 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17D2 MNW‐10‐I2 11/16/2004 15:10 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H6 MNW‐10‐I2‐17 11/8/2004 10:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H5 MNW‐10‐I2‐12 11/8/2004 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H4 MNW‐10‐I2‐7 11/8/2004 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H3 MNW‐10‐I2‐2 11/8/2004 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW10I2Q403 MNW10I2Q403 12/20/2003 12:05 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐11 (D1) 5/10/2020 0:00 unknownMNW-11 (D1) D1 MNW-11-D1-2-082014 MNW-11-D1-2-0 8/25/2014 12:24 PDB GW ug/L 11.3 = 0.5 U 12.8 = 29.0 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐022014 MNW‐11‐D1‐2 2/17/2014 12:20 PDB GW µg/L 10.2 = 0.5 U 11.8 = 23.4 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐0813 MNW‐11‐D1‐2 8/13/2013 9:40 PDB GW µg/L 8.9 = 0.5 U 6.2 = 34.8 = 0.5 UMNW‐11 (D1) D1 F6PB4 MNW‐11‐D1‐2 2/19/2013 0:00 PDB GW µg/L 11 = 0.5 U 9.3 = 36 = 0.14 LJMNW‐11 (D1) D1 F6CE3 MNW‐11‐D1‐2 8/20/2012 13:30 PDB GW µg/L 11 = 0.5 U 5.6 = 46 = 0.5 UMNW‐11 (D1) D1 F5G10DL MNW‐11‐D1‐2 2/27/2012 10:10 PDB GW µg/L 27 =MNW‐11 (D1) D1 F5G10 MNW‐11‐D1‐2 2/27/2012 10:10 PDB GW µg/L 6.3 = 0.5 U 4.2 = 0.5 UMNW‐11 (D1) D1 F4EA8 MNW‐11‐D1‐2‐Q311 8/22/2011 13:17 PDB GW µg/L 10 = 5.0 U 6.6 = 46 = 2.0 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q111 MNW‐11‐D1‐2 2/16/2011 10:30 PDB GW µg/L 8 = 0.5 U 5.6 J 35.2 = 0.5 UMNW‐11 (D1) D1 F3LQ8 MNW‐11‐D1‐2‐Q310 9/2/2010 13:15 PDB GW µg/L 5.9 = 0.5 U 3.8 = 31 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2_100202 MNW‐11‐D1‐2 2/2/2010 9:50 PDB GW µg/L 7.2 = 0.5 U 4.1 = 33.6 = 0.5 UMNW‐11 (D1) D1 F3B26 MNW‐11‐D1‐2 10/26/2009 11:03 PDB GW µg/L 6.9 = 0.5 U 3.7 = 25 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q209 MNW‐11‐D1‐2 4/20/2009 13:30 PDB GW µg/L 6.8 = 0.5 U 3.8 = 33.1 J 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q408 MNW‐11‐D1‐2 10/6/2008 9:35 PDB GW µg/L 7.1 = 0.5 U 3.1 = 32.1 J 0.5 UMNW‐11 (D1) D1 F2RS2 MNW‐11‐D1‐2 4/14/2008 0:00 PDB GW µg/L 7.5 = 0.5 U 4.8 = 20 = 0.5 UMNW‐11 (D1) D1 F2RS3 MNW‐11‐D1‐7 4/14/2008 0:00 PDB GW µg/L 8.6 = 0.5 U 6.2 = 24 = 0.5 UMNW‐11 (D1) D1 F2RS5 MNW‐11‐D1‐17 4/14/2008 0:00 PDB GW µg/L 8.5 = 0.5 U 6 = 25 = 0.5 UMNW‐11 (D1) D1 F2RS4 MNW‐11‐D1‐12 4/14/2008 0:00 PDB GW µg/L 7.1 = 0.5 U 4.8 = 35 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐17‐Q407 MNW‐11‐D1‐17 10/1/2007 9:30 PDB GW µg/L 6.6 = 0.5 U 4.8 = 26.6 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐12‐Q407 MNW‐11‐D1‐12 10/1/2007 9:27 PDB GW µg/L 6.7 = 0.5 U 4.5 = 25.6 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 30 OF 72
011397
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐11 (D1) D1 MNW‐11‐D1‐7‐Q407 MNW‐11‐D1‐7 10/1/2007 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.8 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q407 MNW‐11‐D1‐2 10/1/2007 9:20 PDB GW µg/L 6.3 = 0.5 U 4.2 = 28.1 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐17_070219 MNW‐11‐D1‐17 2/19/2007 14:40 PDB GW µg/L 5.5 JL 0.5 UJ 4.4 JL 22.7 JL 0.5 UJMNW‐11 (D1) D1 MNW‐11‐D1‐12_070219 MNW‐11‐D1‐12 2/19/2007 14:38 PDB GW µg/L 5.5 JL 0.5 UJ 4.3 JL 22.6 JL 0.5 UJMNW‐11 (D1) D1 MNW‐11‐D1‐7_070219 MNW‐11‐D1‐7 2/19/2007 14:35 PDB GW µg/L 5.4 JL 0.5 UJ 4.2 JL 22.9 JL 0.5 UJMNW‐11 (D1) D1 MNW‐11‐D1‐2_070219 MNW‐11‐D1‐2 2/19/2007 14:25 PDB GW µg/L 5.6 JL 0.5 UJ 4.2 JL 24.9 JL 0.5 UJMNW‐11 (D1) D1 F2646DL MNW‐11‐D1‐2 8/29/2006 10:20 PDB GW µg/L 32 =MNW‐11 (D1) D1 F2646 MNW‐11‐D1‐2 8/29/2006 10:20 PDB GW µg/L 4.6 = 0.5 U 0.68 = 0.5 UMNW‐11 (D1) D1 F1YN4 MNW‐11‐D1‐17 2/6/2006 10:00 PDB GW µg/L 5.1 = 0.5 U 5.6 = 16 = 0.5 UMNW‐11 (D1) D1 F1YN3 MNW‐11‐D1‐12 2/6/2006 9:56 PDB GW µg/L 5.2 = 0.5 U 5 = 16 = 0.5 UMNW‐11 (D1) D1 F1YN2 MNW‐11‐D1‐7 2/6/2006 9:53 PDB GW µg/L 4.9 = 0.5 U 4.4 = 17 J 0.5 UMNW‐11 (D1) D1 F1YN1 MNW‐11‐D1‐2 2/6/2006 9:50 PDB GW µg/L 5 = 0.5 U 4.1 = 20 = 0.5 UMNW‐11 (D1) D1 F1NL2 MNW‐11‐D1‐17 7/11/2005 8:33 PDB GW µg/L 3 = 0.5 U 0.14 LJ 13 = 0.5 UMNW‐11 (D1) D1 F1NL1 MNW‐11‐D1‐12 7/11/2005 8:30 PDB GW µg/L 2.2 = 0.5 U 0.5 U 11 = 0.5 UMNW‐11 (D1) D1 F1NL0 MNW‐11‐D1‐7 7/11/2005 8:27 PDB GW µg/L 3.4 = 0.5 U 0.17 LJ 20 = 0.15 LJMNW‐11 (D1) D1 F1NK9DL MNW‐11‐D1‐2 7/11/2005 8:25 PDB GW µg/L 25 =MNW‐11 (D1) D1 F1NK9 MNW‐11‐D1‐2 7/11/2005 8:25 PDB GW µg/L 4.4 = 0.5 U 0.22 LJ 0.12 LJMNW‐11 (D1) D1 F1DG3 MNW‐11‐D1‐17 4/19/2005 10:14 PDB GW µg/L 2.9 = 0.5 U 0.12 LJ 14 = 0.5 UMNW‐11 (D1) D1 F1DG2 MNW‐11‐D1‐12 4/19/2005 10:11 PDB GW µg/L 3 = 0.5 U 0.13 LJ 14 = 0.5 UMNW‐11 (D1) D1 F1DG1 MNW‐11‐D1‐7 4/19/2005 10:09 PDB GW µg/L 3.1 = 0.5 U 0.12 LJ 14 = 0.5 UMNW‐11 (D1) D1 F1DG0 MNW‐11‐D1‐2 4/19/2005 10:06 PDB GW µg/L 2.8 = 0.5 U 0.13 LJ 14 = 0.5 U
MNW‐11 (D2) 5/10/2020 0:00 unknownMNW‐11 (D2) D2 F6PB5 MNW‐11‐D2‐2 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F5G12 MNW‐11‐D2‐17 2/27/2012 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.099 LJ 0.5 UMNW‐11 (D2) D2 F5G11 MNW‐11‐D2‐12 2/27/2012 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐11 (D2) D2 F5G14 MNW‐11‐D2‐7 2/27/2012 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.097 LJ 0.5 UMNW‐11 (D2) D2 F5G13 MNW‐11‐D2‐2 2/27/2012 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.15 LJ 0.5 UMNW‐11 (D2) D2 F4EB0 MNW‐11‐D2‐17‐Q311 8/22/2011 13:10 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 F4EA9 MNW‐11‐D2‐12‐Q311 8/22/2011 13:08 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 F4EB2 MNW‐11‐D2‐7‐Q311 8/22/2011 13:06 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 F4EB1 MNW‐11‐D2‐2‐Q311 8/22/2011 13:05 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 MNW‐11‐D2‐17‐Q111 MNW‐11‐D2‐17 2/16/2011 10:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 MNW‐11‐D2‐12‐Q111 MNW‐11‐D2‐12 2/16/2011 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 MNW‐11‐D2‐7‐Q111 MNW‐11‐D2‐7 2/16/2011 10:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 MNW‐11‐D2‐2‐Q111 MNW‐11‐D2‐2 2/16/2011 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1NL6 MNW‐11‐D2‐17 7/11/2005 8:52 PDB GW µg/L 0.5 U 0.22 LJ 0.5 U 0.14 LJ 0.5 UMNW‐11 (D2) D2 F1NL5 MNW‐11‐D2‐12 7/11/2005 8:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1NL4 MNW‐11‐D2‐7 7/11/2005 8:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1NL3 MNW‐11‐D2‐2 7/11/2005 8:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐11 (D2) D2 F1DG7 MNW‐11‐D2‐17 4/19/2005 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 31 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐11 (D2) D2 F1DG6 MNW‐11‐D2‐12 4/19/2005 10:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1DG5 MNW‐11‐D2‐7 4/19/2005 10:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1DG4 MNW‐11‐D2‐2 4/19/2005 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐11 (I1) 5/10/2020 0:00 unknownMNW‐11 (I1) I1 F6PB6 MNW‐11‐I1‐7 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.33 LJ 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐7‐Q111 MNW‐11‐I1‐7 2/16/2011 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐7‐Q209 MNW‐11‐I1‐7 4/20/2009 13:05 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.7 = 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐7‐Q408 MNW‐11‐I1‐7 10/6/2008 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐11 (I1) I1 F2RR9 MNW‐11‐I1‐7 4/14/2008 0:00 PDB GW µg/L 0.37 LJ 0.5 U 0.5 U 0.88 = 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐7‐Q407 MNW‐11‐I1‐7 10/1/2007 9:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1_070219 MNW‐11‐I1‐7 2/19/2007 14:19 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.7 JL 0.5 UJMNW‐11 (I1) I1 F2647 MNW‐11‐I1‐7 8/29/2006 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I1) I1 F1YM7 MNW‐11‐I1‐7 2/6/2006 9:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.66 = 0.5 UMNW‐11 (I1) I1 F1NK7 MNW‐11‐I1‐12 7/11/2005 9:02 PDB GW µg/L 0.27 LJ 0.5 U 0.5 U 0.59 = 0.5 UMNW‐11 (I1) I1 F1NK6 MNW‐11‐I1‐7 7/11/2005 9:00 PDB GW µg/L 0.31 LJ 0.5 U 0.5 U 0.86 = 0.5 UMNW‐11 (I1) I1 F1NK5 MNW‐11‐I1‐2 7/11/2005 8:58 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.77 = 0.5 UMNW‐11 (I1) I1 F1DF6 MNW‐11‐I1‐12 4/19/2005 9:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.43 LJ 0.5 UMNW‐11 (I1) I1 F1DF4 MNW‐11‐I1‐7 4/19/2005 9:35 PDB GW µg/L 0.23 LJ 0.5 U 0.5 U 0.63 = 0.5 UMNW‐11 (I1) I1 F1DF3 MNW‐11‐I1‐2 4/19/2005 9:32 PDB GW µg/L 0.23 LJ 0.5 U 0.5 U 0.64 = 0.5 U
MNW‐11 (I2) 5/10/2020 0:00 unknownMNW‐11 (I2) I2 F6PB7 MNW‐11‐I2‐12 2/19/2013 0:00 PDB GW µg/L 0.55 = 0.5 U 0.23 LJ 0.63 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐Q111 MNW‐11‐I2‐12 2/16/2011 10:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐FD‐Q209 MNW‐11‐I2‐12‐FD 4/20/2009 13:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐Q209 MNW‐11‐I2‐12 4/20/2009 13:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐Q408 MNW‐11‐I2‐12 10/6/2008 9:42 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.7 = 0.5 UMNW‐11 (I2) I2 F2RS0 MNW‐11‐I2‐12 4/14/2008 0:00 PDB GW µg/L 0.79 = 0.5 U 0.49 LJ 0.92 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐Q407 MNW‐11‐I2‐12 10/1/2007 9:13 PDB GW µg/L 0.8 = 0.5 U 0.6 = 1.1 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2_070219 MNW‐11‐I2‐12 2/19/2007 14:50 PDB GW µg/L 0.9 JL 0.5 UJ 0.7 JL 1.4 JL 0.5 UJMNW‐11 (I2) I2 F2648 MNW‐11‐I2‐12 8/29/2006 10:10 PDB GW µg/L 0.69 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐11 (I2) I2 F1YN0 MNW‐11‐I2‐12 2/6/2006 9:42 PDB GW µg/L 1.2 = 0.5 U 0.5 U 3.5 = 0.5 UMNW‐11 (I2) I2 F1YM8 MNW‐11‐I2‐2 2/6/2006 9:40 PDB GW µg/L 0.68 = 0.5 U 0.5 U 2 = 0.5 UMNW‐11 (I2) I2 F1NK8 MNW‐11‐I2‐12 7/11/2005 9:35 PDB GW µg/L 1.4 = 0.5 U 0.5 U 3.7 = 0.5 UMNW‐11 (I2) I2 F1NK3 MNW‐11‐I2‐7 7/11/2005 9:31 PDB GW µg/L 1.4 = 0.5 U 0.5 U 3.8 = 0.5 UMNW‐11 (I2) I2 F1NK2 MNW‐11‐I2‐2 7/11/2005 9:30 PDB GW µg/L 1 = 0.5 U 0.5 U 2.3 = 0.5 UMNW‐11 (I2) I2 F1P97 MNW‐11‐I2‐17 7/11/2005 9:27 PDB GW µg/L 1.3 = 0.5 U 0.5 U 3.7 = 0.5 UMNW‐11 (I2) I2 F1DF9 MNW‐11‐I2‐12 4/19/2005 9:58 PDB GW µg/L 0.96 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐11 (I2) I2 F1DF8 MNW‐11‐I2‐7 4/19/2005 9:55 PDB GW µg/L 0.97 = 0.5 U 0.05 LJ 3 = 0.5 UMNW‐11 (I2) I2 F1DF7 MNW‐11‐I2‐2 4/19/2005 9:53 PDB GW µg/L 0.64 = 0.5 U 0.5 U 1.8 = 0.5 U
MNW‐12 (D1) 5/10/2020 0:00 unknownMNW‐12 (D1) D1 MNW‐12‐D1‐12‐022014 MNW‐12‐D1‐12 2/17/2014 12:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 32 OF 72
011399
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐12 (D1) D1 F6PB8 MNW‐12‐D1‐12 2/19/2013 0:00 PDB GW µg/L 0.58 = 0.5 U 0.5 U 1.1 = 0.5 UMNW‐12 (D1) D1 F6PB9 MNW‐12‐D1‐12‐FD 2/19/2013 0:00 PDB GW µg/L 0.64 = 0.5 U 0.5 U 1.2 = 0.5 UMNW‐12 (D1) D1 F5G15 MNW‐12‐D1‐12 2/27/2012 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q111‐FD MNW‐12‐D1‐12 2/16/2011 9:25 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q111 MNW‐12‐D1‐12 2/16/2011 9:20 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12_100202 MNW‐12‐D1‐12 2/2/2010 10:10 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.3 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q408 MNW‐12‐D1‐12 10/6/2008 8:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.6 = 0.5 UMNW‐12 (D1) D1 F2RS7 MNW‐12‐D1‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q407 MNW‐12‐D1‐12 10/1/2007 10:00 PDB GW µg/L 0.9 = 0.5 U 0.5 U 3.2 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12_070219 MNW‐12‐D1‐12 2/19/2007 14:58 PDB GW µg/L 0.9 JL 0.5 UJ 0.5 UJ 3.1 JL 0.5 UJMNW‐12 (D1) D1 F2650 MNW‐12‐D1‐12 8/29/2006 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.2 J 0.5 UMNW‐12 (D1) D1 F1YN8 MNW‐12‐D1‐17 2/6/2006 11:50 PDB GW µg/L 0.71 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐12 (D1) D1 F1YN7 MNW‐12‐D1‐12 2/6/2006 11:48 PDB GW µg/L 0.71 = 0.5 U 0.5 U 2.9 = 0.5 UMNW‐12 (D1) D1 F1YN6 MNW‐12‐D1‐7 2/6/2006 11:46 PDB GW µg/L 0.64 = 0.5 U 0.5 U 2.5 = 0.5 UMNW‐12 (D1) D1 F1NM7 MNW‐12‐D1‐17 7/11/2005 10:56 PDB GW µg/L 0.52 = 0.5 U 0.5 U 2.9 J 0.5 UMNW‐12 (D1) D1 F1NM5 MNW‐12‐D1‐12 7/11/2005 10:53 PDB GW µg/L 0.46 LJ 0.5 U 0.5 U 3.1 = 0.5 UMNW‐12 (D1) D1 F1NM4 MNW‐12‐D1‐7 7/11/2005 10:51 PDB GW µg/L 0.73 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐12 (D1) D1 F1NM3 MNW‐12‐D1‐2 7/11/2005 10:50 PDB GW µg/L 0.76 = 0.5 U 0.5 U 1.8 = 0.1 LJMNW‐12 (D1) D1 F1DH8 MNW‐12‐D1‐17 4/18/2005 15:11 PDB GW µg/L 0.48 LJ 0.5 U 0.5 U 1.5 J 0.5 UMNW‐12 (D1) D1 F1DH6 MNW‐12‐D1‐12 4/18/2005 15:04 PDB GW µg/L 0.4 LJ 0.5 U 0.5 U 1.5 = 0.5 UMNW‐12 (D1) D1 F1DH5 MNW‐12‐D1‐7 4/18/2005 14:57 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 1.5 = 0.5 UMNW‐12 (D1) D1 F1DH4 MNW‐12‐D1‐2 4/18/2005 14:54 PDB GW µg/L 0.41 LJ 0.5 U 0.5 U 1.4 = 0.5 U
MNW‐12 (D2) 5/10/2020 0:00 unknownMNW‐12 (D2) D2 F6PC0 MNW‐12‐D2‐7 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G20 MNW‐12‐D2‐7 2/27/2012 8:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G19 MNW‐12‐D2‐2 2/27/2012 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G18 MNW‐12‐D2‐17 2/27/2012 8:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G17 MNW‐12‐D2‐12‐FD 2/27/2012 8:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G16 MNW‐12‐D2‐12 2/27/2012 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F4EB4 MNW‐12‐D2‐17‐Q311 8/22/2011 9:49 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 F4EB3 MNW‐12‐D2‐12‐Q311 8/22/2011 9:47 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 F4EB6 MNW‐12‐D2‐7‐Q311 8/22/2011 9:46 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 F4EB5 MNW‐12‐D2‐2‐Q311 8/22/2011 9:45 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 MNW‐12‐D2‐17‐Q111 MNW‐12‐D2‐17 2/16/2011 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 MNW‐12‐D2‐12‐Q111 MNW‐12‐D2‐12 2/16/2011 9:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 MNW‐12‐D1‐7‐Q111 MNW‐12‐D2‐7 2/16/2011 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 MNW‐12‐D2‐2‐Q111 MNW‐12‐D2‐2 2/16/2011 9:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1NN1 MNW‐12‐D2‐17 7/11/2005 11:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1NN0 MNW‐12‐D2‐12 7/11/2005 11:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1NM9 MNW‐12‐D2‐7 7/11/2005 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 33 OF 72
011400
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐12 (D2) D2 F1NM8 MNW‐12‐D2‐2 7/11/2005 11:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1DJ2 MNW‐12‐D2‐17 4/18/2005 15:31 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 0.5 U 0.16 LJMNW‐12 (D2) D2 F1DJ1 MNW‐12‐D2‐12 4/18/2005 15:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1DJ0 MNW‐12‐D2‐7 4/18/2005 15:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1DH9 MNW‐12‐D2‐2 4/18/2005 15:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐12 (I1) 5/10/2020 0:00 unknownMNW‐12 (I1) I1 F6PC1 MNW‐12‐I1‐12 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F5G23 MNW‐12‐I1‐12 2/27/2012 8:52 PDB GW µg/L 0.49 LJ 0.5 U 0.5 U 0.75 = 0.5 UMNW‐12 (I1) I1 F5G22 MNW‐12‐I1‐7 2/27/2012 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F5G21 MNW‐12‐I1‐2 2/27/2012 8:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F4EB9 MNW‐12‐I1‐12‐Q311 8/22/2011 10:07 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 F4EB8 MNW‐12‐I1‐7‐FD‐Q311 8/22/2011 10:06 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 F4EB7 MNW‐12‐I1‐7‐Q311 8/22/2011 10:05 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 F4ED3 MNW‐12‐I1‐2‐Q311 8/22/2011 10:04 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 MNW‐12‐I1‐8‐Q111 MNW‐12‐I1‐12 2/16/2011 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 MNW‐12‐I1‐5‐Q111 MNW‐12‐I1‐7 2/16/2011 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 MNW‐12‐I1‐2‐Q111 MNW‐12‐I1‐2 2/16/2011 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1NL9 MNW‐12‐I1‐12 7/11/2005 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1NL8 MNW‐12‐I1‐7 7/11/2005 10:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1NL7 MNW‐12‐I1‐2 7/11/2005 10:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1DH0 MNW‐12‐I1‐12 4/18/2005 14:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1DG9 MNW‐12‐I1‐7 4/18/2005 14:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1DG8 MNW‐12‐I1‐2 4/18/2005 14:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐12 (I2) 5/10/2020 0:00 unknownMNW‐12 (I2) I2 F6PC2 MNW‐12‐I2‐7 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐7‐Q111 MNW‐12‐I2‐7 2/16/2011 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐7‐Q209 MNW‐12‐I2‐7 4/20/2009 14:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐7‐Q408 MNW‐12‐I2‐7 10/6/2008 8:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F2RS6 MNW‐12‐I2‐7 4/14/2008 0:00 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2.3 = 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐7‐Q407 MNW‐12‐I2‐7 10/1/2007 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2_070219 MNW‐12‐I2‐7 2/19/2007 14:49 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐12 (I2) I2 F2651 MNW‐12‐I2‐7 8/29/2006 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1YN5 MNW‐12‐I2‐7 2/6/2006 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1NM2 MNW‐12‐I2‐12 7/11/2005 10:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1NM1 MNW‐12‐I2‐7 7/11/2005 10:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1NM0 MNW‐12‐I2‐2 7/11/2005 10:39 PDB GW µg/L 0.5 U 0.13 LJ 0.5 U 0.5 U 0.11 LJMNW‐12 (I2) I2 F1DH3 MNW‐12‐I2‐12 4/18/2005 14:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1DH2 MNW‐12‐I2‐7 4/18/2005 14:42 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐12 (I2) I2 F1DH1 MNW‐12‐I2‐2 4/18/2005 14:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐13 (D1) 5/10/2020 0:00 unknown
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 34 OF 72
011401
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐13 (D1) D1 MNW‐13‐D1‐7‐022014 MNW‐13‐D1‐7 2/18/2014 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 UMNW‐13 (D1) D1 F6PC3 MNW‐13‐D1‐7 2/12/2013 0:00 PDB GW µg/L 0.34 LJ 0.32 LJ 0.5 U 1.1 = 0.5 UMNW‐13 (D1) D1 F5G24 MNW‐13‐D1‐7 2/28/2012 13:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.4 = 0.5 UMNW‐13 (D1) D1 F3S12 MNW‐13‐D1‐7 2/15/2011 8:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1‐12_100201 MNW‐13‐D1‐12 2/1/2010 11:08 PDB GW µg/L 0.5 = 0.8 = 0.5 U 1.9 = 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1‐7‐Q209 MNW‐13‐D1‐7 4/21/2009 12:35 PDB GW µg/L 0.5 J 0.9 J 0.5 UJ 2.0 J 0.5 UJMNW‐13 (D1) D1 MNW‐13‐D1‐7‐Q408 MNW‐13‐D1‐7 10/6/2008 14:12 PDB GW µg/L 0.5 = 0.7 = 0.5 U 2 = 0.5 UMNW‐13 (D1) D1 F2RS8 MNW‐13‐D1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.6 = 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1‐7‐Q407 MNW‐13‐D1‐7 10/2/2007 11:25 PDB GW µg/L 0.6 = 1 = 0.5 U 2.5 = 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1_070219 MNW‐13‐D1‐7 2/19/2007 11:22 PDB GW µg/L 0.5 UJ 0.6 JL 0.5 UJ 1.8 JL 0.5 UJMNW‐13 (D1) D1 F2652 MNW‐13‐D1‐7 8/29/2006 7:20 PDB GW µg/L 0.5 U 0.58 = 0.5 U 1.8 = 0.5 UMNW‐13 (D1) D1 F1YT0 MNW‐13‐D1‐7 2/6/2006 9:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D1) D1 F1P22 MNW‐13‐D1‐17 7/11/2005 8:44 PDB GW µg/L 0.43 LJ 1 = 0.18 LJ 3.4 = 0.5 UMNW‐13 (D1) D1 F1P20 MNW‐13‐D1‐12 7/11/2005 8:42 PDB GW µg/L 0.36 LJ 0.92 = 0.12 LJ 2.7 = 0.5 UMNW‐13 (D1) D1 F1P19 MNW‐13‐D1‐7 7/11/2005 8:38 PDB GW µg/L 0.39 LJ 0.7 = 0.18 LJ 2.9 = 0.5 UMNW‐13 (D1) D1 F1DX0 MNW‐13‐D1‐17 4/18/2005 11:00 PDB GW µg/L 0.76 = 1.2 = 0.5 U 3.6 = 0.5 UMNW‐13 (D1) D1 F1DW9 MNW‐13‐D1‐12 4/18/2005 10:58 PDB GW µg/L 0.79 = 1.1 = 0.17 LJ 3.6 = 0.5 UMNW‐13 (D1) D1 F1DW8 MNW‐13‐D1‐7 4/18/2005 10:56 PDB GW µg/L 0.67 = 0.74 = 0.22 LJ 3.1 = 0.5 U
MNW‐13 (D2) 5/10/2020 0:00 unknownMNW‐13 (D2) D2 MNW‐13‐D2‐7‐022014 MNW‐13‐D2‐7 2/18/2014 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7‐022014‐FD MNW‐13‐D2‐7‐FD 2/18/2014 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F6PC4 MNW‐13‐D2‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F6PC5 MNW‐13‐D2‐7‐FD 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F5G25 MNW‐13‐D2‐7 2/28/2012 14:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F3S14 MNW‐13‐D2‐7 2/15/2011 10:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F3S13 MNW‐13‐D2‐7 2/15/2011 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7_100201 MNW‐13‐D2‐7 2/1/2010 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7‐Q209 MNW‐13‐D2‐7 4/21/2009 12:46 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D2) D2 MNW‐13‐D2‐7‐Q408 MNW‐13‐D2‐7 10/6/2008 13:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F2RS9 MNW‐13‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7‐Q407 MNW‐13‐D2‐7 10/2/2007 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2_070219 MNW‐13‐D2‐7 2/19/2007 11:40 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D2) D2 F2653 MNW‐13‐D2‐7 8/29/2006 7:40 PDB GW µg/L 0.68 = 0.5 U 0.5 U 1.5 = 0.5 UMNW‐13 (D2) D2 F1YT1 MNW‐13‐D2‐7 2/6/2006 9:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P26 MNW‐13‐D2‐17 7/11/2005 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P25 MNW‐13‐D2‐12 7/11/2005 9:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P24 MNW‐13‐D2‐7 7/11/2005 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P23 MNW‐13‐D2‐2 7/11/2005 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1DX4 MNW‐13‐D2‐17 4/18/2005 9:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1DX3 MNW‐13‐D2‐12 4/18/2005 9:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 35 OF 72
011402
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐13 (D2) D2 F1DX2 MNW‐13‐D2‐7 4/18/2005 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1DX1 MNW‐13‐D2‐2 4/18/2005 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐13 (D3) 5/10/2020 0:00 unknownMNW‐13 (D3) D3 MNW‐13‐D3‐7‐022014 MNW‐13‐D3‐7 2/18/2014 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F6PC6 MNW‐13‐D3‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F5G26 MNW‐13‐D3‐7 2/28/2012 14:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F3S15 MNW‐13‐D3‐7 2/15/2011 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3‐7_100201 MNW‐13‐D3‐7 2/1/2010 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3‐7‐Q209 MNW‐13‐D3‐7 4/21/2009 13:07 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D3) D3 MNW‐13‐D3‐7‐Q408 MNW‐13‐D3‐7 10/6/2008 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F2RT0 MNW‐13‐D3‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3‐7‐Q407 MNW‐13‐D3‐7 10/2/2007 11:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3_070219 MNW‐13‐D3‐7 2/19/2007 11:55 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D3) D3 F2654 MNW‐13‐D3‐7 8/29/2006 8:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJMNW‐13 (D3) D3 F1YT2 MNW‐13‐D3‐7 2/6/2006 9:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1P30 MNW‐13‐D3‐17 7/11/2005 9:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1P28 MNW‐13‐D3‐7 7/11/2005 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1P29 MNW‐13‐D3‐12 7/11/2005 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1P27 MNW‐13‐D3‐2 7/11/2005 9:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX8 MNW‐13‐D3‐17 4/18/2005 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX7 MNW‐13‐D3‐12 4/18/2005 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX6 MNW‐13‐D3‐7 4/18/2005 10:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX5 MNW‐13‐D3‐2 4/18/2005 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐13 (D4) 5/10/2020 0:00 unknownMNW‐13 (D4) D4 MNW‐13‐D4‐7‐FD‐Q209 MNW‐13‐D4‐7‐FD 4/21/2009 13:06 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D4) D4 MNW‐13‐D4‐7‐Q209 MNW‐13‐D4‐7 4/21/2009 13:05 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D4) D4 MNW‐13‐D4‐7‐Q408 MNW‐13‐D4‐7 10/6/2008 14:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F2RT1 MNW‐13‐D4‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 MNW‐13‐D4‐7‐Q407 MNW‐13‐D4‐7 10/2/2007 12:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 MNW‐13‐D4_070219 MNW‐13‐D4‐7 2/19/2007 12:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D4) D4 F2655 MNW‐13‐D4‐7 8/29/2006 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1YT4 MNW‐13‐D4‐12 2/6/2006 9:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1YT3 MNW‐13‐D4‐7 2/6/2006 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P33 MNW‐13‐D4‐12 7/11/2005 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P34 MNW‐13‐D4‐17 7/11/2005 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P32 MNW‐13‐D4‐7 7/11/2005 9:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P31 MNW‐13‐D4‐2 7/11/2005 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1DY2 MNW‐13‐D4‐17 4/18/2005 9:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1DY1 MNW‐13‐D4‐12 4/18/2005 9:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1DY0 MNW‐13‐D4‐7 4/18/2005 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 36 OF 72
011403
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐13 (D4) D4 F1DX9 MNW‐13‐D4‐2 4/18/2005 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) 5/10/2020 0:00 unknown
MNW-14 (D1) D1 MNW-14-D1-7-0814 MNW-14-D1-7 8/25/2014 9:56 PDB GW ug/L 0.5 U 0.5 U 0.5 U 1.6 = 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐022014 MNW‐14‐D1‐7 2/17/2014 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐0813 MNW‐14‐D1‐7 8/12/2013 9:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.7 = 0.5 UMNW‐14 (D1) D1 F6PC7 MNW‐14‐D1‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.86 = 0.5 UMNW‐14 (D1) D1 F6CA5 MNW‐14‐D1‐7 8/20/2012 10:05 PDB GW µg/L 0.16 LJ 0.5 U 0.5 U 0.74 = 0.5 UMNW‐14 (D1) D1 F5G83 MNW‐14‐D1‐7 2/27/2012 9:53 PDB GW µg/L 0.22 LJ 0.5 U 0.5 U 1.8 = 0.5 UMNW‐14 (D1) D1 F4EC0 MNW‐14‐D1‐7‐Q311 8/22/2011 12:25 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐Q111 MNW‐14‐D1‐7 2/14/2011 11:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐Q408 MNW‐14‐D1‐7 10/6/2008 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F2RY4 MNW‐14‐D1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐Q407 MNW‐14‐D1‐7 10/2/2007 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1_070219 MNW‐14‐D1‐7 2/19/2007 9:10 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐14 (D1) D1 F2657 MNW‐14‐D1‐7 8/29/2006 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1YQ3 MNW‐14‐D1‐7 2/6/2006 13:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP5 MNW‐14‐D1‐17 7/12/2005 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP4 MNW‐14‐D1‐12 7/12/2005 9:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP3 MNW‐14‐D1‐7 7/12/2005 9:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP1 MNW‐14‐D1‐2 7/12/2005 9:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK6 MNW‐14‐D1‐17 4/18/2005 11:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK5 MNW‐14‐D1‐12 4/18/2005 11:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK4 MNW‐14‐D1‐7 4/18/2005 11:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK2 MNW‐14‐D1‐2 4/18/2005 11:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐14 (D2) 5/10/2020 0:00 unknownMNW‐14 (D2) D2 MNW‐14‐D2‐17‐Q209 MNW‐14‐D2‐17 4/20/2009 11:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐2‐Q209 MNW‐14‐D2‐2 4/20/2009 11:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐17‐Q408 MNW‐14‐D2‐17 10/6/2008 9:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐2‐Q408 MNW‐14‐D2‐2 10/6/2008 9:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 F2RY6 MNW‐14‐D2‐17 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.29 LJ 0.19 LJ 0.5 UMNW‐14 (D2) D2 F2RY5 MNW‐14‐D2‐2 4/14/2008 0:00 PDB GW µg/L 0.18 LJ 0.5 U 0.3 LJ 0.19 LJ 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐17‐Q407 MNW‐14‐D2‐17 10/2/2007 9:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐2‐Q407 MNW‐14‐D2‐2 10/2/2007 9:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐17_070219 MNW‐14‐D2‐17 2/19/2007 9:25 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐14 (D2) D2 MNW‐14‐D2‐2_070219 MNW‐14‐D2‐2 2/19/2007 9:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐14 (D2) D2 F2658 MNW‐14‐D2‐17 8/29/2006 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 F2659 MNW‐14‐D2‐2 8/29/2006 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 F1YQ5 MNW‐14‐D2‐17 2/6/2006 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.74 = 0.5 UMNW‐14 (D2) D2 F1YQ4 MNW‐14‐D2‐2 2/6/2006 13:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.74 = 0.5 UMNW‐14 (D2) D2 F1NP9 MNW‐14‐D2‐17 7/12/2005 9:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.92 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 37 OF 72
011404
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐14 (D2) D2 F1NP8 MNW‐14‐D2‐12 7/12/2005 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.75 = 0.5 UMNW‐14 (D2) D2 F1NP7 MNW‐14‐D2‐7 7/12/2005 9:51 PDB GW µg/L 0.11 LJ 0.5 U 0.5 U 0.73 = 0.5 UMNW‐14 (D2) D2 F1NP6 MNW‐14‐D2‐2 7/12/2005 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.82 = 0.5 UMNW‐14 (D2) D2 F1DL0 MNW‐14‐D2‐17 4/18/2005 11:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.67 = 0.5 UMNW‐14 (D2) D2 F1DK9 MNW‐14‐D2‐12 4/18/2005 11:49 PDB GW µg/L 0.12 LJ 0.5 U 0.5 U 0.67 = 0.5 UMNW‐14 (D2) D2 F1DK8 MNW‐14‐D2‐7 4/18/2005 11:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.66 = 0.5 UMNW‐14 (D2) D2 F1DK7 MNW‐14‐D2‐2 4/18/2005 11:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.78 = 0.5 U
MNW‐14 (I2) 5/10/2020 0:00 unknownMNW-14 (I2) I2 MNW-14-I2-2-0814-FD MNW-14-I2-2 8/25/2014 10:48 PDB GW ug/L 7.9 = 0.5 U 1.2 = 44.2 = 0.5 UMNW-14 (I2) I2 MNW-14-I2-8-0814 MNW-14-I2-8 8/25/2014 9:50 PDB GW ug/L 8.1 = 0.5 U 1.1 = 39.3 = 0.5 UMNW-14 (I2) I2 MNW-14-I2-2-0814 MNW-14-I2-2 8/25/2014 9:48 PDB GW ug/L 7.9 = 0.5 U 1.3 = 44.8 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐022014 MNW‐14‐I2‐8 2/17/2014 10:49 PDB GW µg/L 7.7 = 0.5 U 1.1 = 38.2 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐022014 MNW‐14‐I2‐2 2/17/2014 10:44 PDB GW µg/L 7.6 = 0.5 U 1.1 = 32.4 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐0813 MNW‐14‐I2‐2 8/12/2013 9:22 PDB GW µg/L 8.4 = 0.5 U 1.1 = 36.8 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐0813 MNW‐14‐I2‐8 8/12/2013 9:20 PDB GW µg/L 7.7 = 0.5 U 0.9 = 42.8 = 0.5 UMNW‐14 (I2) I2 F6PC8 MNW‐14‐I2‐2 2/13/2013 0:00 PDB GW µg/L 9.2 = 0.5 U 0.99 = 33 = 0.5 UMNW‐14 (I2) I2 F6PC9 MNW‐14‐I2‐8 2/13/2013 0:00 PDB GW µg/L 8.8 = 0.5 U 0.85 = 39 = 0.5 UMNW‐14 (I2) I2 F6CA7 MNW‐14‐I2‐8 8/20/2012 10:21 PDB GW µg/L 7.6 = 0.16 LJ 0.70 LJ 48 = 2.5 UMNW‐14 (I2) I2 F6CA6 MNW‐14‐I2‐2 8/20/2012 10:18 PDB GW µg/L 8.1 = 2.5 U 0.69 LJ 46 = 2.5 UMNW‐14 (I2) I2 F5G85DL MNW‐14‐I2‐8 2/27/2012 9:40 PDB GW µg/L 35 =MNW‐14 (I2) I2 F5G85 MNW‐14‐I2‐8 2/27/2012 9:40 PDB GW µg/L 7.8 = 0.5 U 0.93 = 0.5 UMNW‐14 (I2) I2 F5G84DL MNW‐14‐I2‐2 2/27/2012 9:38 PDB GW µg/L 39 =MNW‐14 (I2) I2 F5G84 MNW‐14‐I2‐2 2/27/2012 9:38 PDB GW µg/L 8.6 = 0.5 U 3 = 0.5 UMNW‐14 (I2) I2 F4EC2 MNW‐14‐I2‐8‐Q311 8/22/2011 12:40 PDB GW µg/L 9.7 = 5.0 U 5.0 U 51 = 2.0 UMNW‐14 (I2) I2 F4EC1 MNW‐14‐I2‐2‐Q311 8/22/2011 12:35 PDB GW µg/L 11 = 5.0 U 1.3 LJ 44 = 2.0 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q111 MNW‐14‐I2‐8 2/14/2011 11:07 PDB GW µg/L 6.5 = 0.5 U 2 = 26.2 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q111 MNW‐14‐I2‐2 2/14/2011 11:06 PDB GW µg/L 7.4 = 0.5 U 0.8 = 32.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q310 MNW‐14‐I2‐8‐Q310 9/7/2010 13:35 PDB GW µg/L 8.2 = 0.5 U 1.2 = 30.0 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q310 MNW‐14‐I2‐2‐Q310 9/7/2010 13:30 PDB GW µg/L 8.8 = 0.5 U 1.1 = 32.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8_100201 MNW‐14‐I2‐8 2/1/2010 11:18 PDB GW µg/L 8.1 = 0.5 U 0.6 = 34.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2_100201 MNW‐14‐I2‐2 2/1/2010 11:15 PDB GW µg/L 8.8 = 0.5 U 0.7 = 31.7 = 0.5 UMNW‐14 (I2) I2 F3B79 MNW‐14‐I2‐8 10/26/2009 13:03 PDB GW µg/L 9.1 = 0.5 U 0.66 = 32 = 0.5 UMNW‐14 (I2) I2 F3B78 MNW‐14‐I2‐2 10/26/2009 13:00 PDB GW µg/L 7.8 = 0.5 U 0.61 = 37 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q209 MNW‐14‐I2‐8 4/20/2009 11:47 PDB GW µg/L 9.2 = 0.5 U 0.9 = 36.9 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐FD‐Q209 MNW‐14‐I2‐2‐FD 4/20/2009 11:45 PDB GW µg/L 8.0 = 0.5 U 0.7 = 30.7 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q209 MNW‐14‐I2‐2 4/20/2009 11:44 PDB GW µg/L 8.1 = 0.5 U 0.8 = 32.6 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q408 MNW‐14‐I2‐8 10/6/2008 8:43 PDB GW µg/L 9.6 = 0.5 U 0.7 = 32.5 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q408 MNW‐14‐I2‐2 10/6/2008 8:36 PDB GW µg/L 8.2 = 0.5 U 0.7 = 29.7 = 0.5 UMNW‐14 (I2) I2 F2RY3 MNW‐14‐I2‐8 4/14/2008 0:00 PDB GW µg/L 6.9 = 0.5 U 0.74 = 20 = 0.5 UMNW‐14 (I2) I2 F2RZ2 MNW‐14‐I2‐2 4/14/2008 0:00 PDB GW µg/L 8.7 = 0.5 U 0.82 = 21 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 38 OF 72
011405
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q407 MNW‐14‐I2‐8 10/2/2007 9:24 PDB GW µg/L 7.2 = 0.5 U 0.7 = 29.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q407 MNW‐14‐I2‐2 10/2/2007 9:20 PDB GW µg/L 6.6 = 0.5 U 0.7 = 25.2 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2_070219 MNW‐14‐I2‐2 2/19/2007 9:50 PDB GW µg/L 5.1 JL 0.5 UJ 0.7 JL 22.8 JL 0.5 UJMNW‐14 (I2) I2 MNW‐14‐I2‐8_070219 MNW‐14‐I2‐8 2/19/2007 9:45 PDB GW µg/L 5.9 JL 0.5 UJ 0.7 JL 26.5 JL 0.5 UJMNW‐14 (I2) I2 F2662 MNW‐14‐I2‐8 8/29/2006 8:40 PDB GW µg/L 2.8 = 0.5 U 0.5 U 15 = 0.5 UMNW‐14 (I2) I2 F2660 MNW‐14‐I2‐2 8/29/2006 8:37 PDB GW µg/L 3.1 = 0.5 U 0.5 U 17 = 0.5 UMNW‐14 (I2) I2 F1YQ2 MNW‐14‐I2‐8 2/6/2006 13:27 PDB GW µg/L 4.4 = 0.5 U 0.6 = 20 = 0.5 UMNW‐14 (I2) I2 F1YQ1 MNW‐14‐I2‐5 2/6/2006 13:25 PDB GW µg/L 4.1 = 0.5 U 0.71 = 16 = 0.5 UMNW‐14 (I2) I2 F1YP9 MNW‐14‐I2‐2 2/6/2006 13:18 PDB GW µg/L 4 = 0.5 U 0.59 = 17 = 0.5 UMNW‐14 (I2) I2 F1NN9 MNW‐14‐I2‐8 7/12/2005 10:07 PDB GW µg/L 5.4 = 0.5 U 0.71 = 23 = 0.1 LJMNW‐14 (I2) I2 F1NN8 MNW‐14‐I2‐5 7/12/2005 10:05 PDB GW µg/L 5.2 = 0.5 U 0.84 = 22 = 0.16 LJMNW‐14 (I2) I2 F1NN7 MNW‐14‐I2‐2 7/12/2005 10:03 PDB GW µg/L 4.7 = 0.8 U 0.62 LJ 24 = 0.8 UMNW‐14 (I2) I2 F1DK0 MNW‐14‐I2‐8 4/18/2005 11:03 PDB GW µg/L 3.5 J 0.5 U 0.43 LJ 11 J 0.5 UMNW‐14 (I2) I2 F1DJ9DL MNW‐14‐I2‐5 4/18/2005 10:57 PDB GW µg/L 16 =MNW‐14 (I2) I2 F1DJ9 MNW‐14‐I2‐5 4/18/2005 10:57 PDB GW µg/L 5.9 = 0.5 U 0.88 J 0.2 LJMNW‐14 (I2) I2 F1DJ8DL MNW‐14‐I2‐2 4/18/2005 10:50 PDB GW µg/L 25 =MNW‐14 (I2) I2 F1DJ8 MNW‐14‐I2‐2 4/18/2005 10:50 PDB GW µg/L 6.7 = 0.5 U 0.93 J 0.23 LJ
MNW‐15 (D1) 5/10/2020 0:00 unknownMNW‐15 (D1) D1 F6PD0 MNW‐15‐D1‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F5G28 MNW‐15‐D1‐7‐FD 2/28/2012 14:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F5G27 MNW‐15‐D1‐7 2/28/2012 13:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F3S16 MNW‐15‐D1‐7 2/15/2011 12:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7_100201 MNW‐15‐D1‐7 2/1/2010 7:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7‐Q209 MNW‐15‐D1‐7 4/20/2009 13:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7‐Q408 MNW‐15‐D1‐7 10/6/2008 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2RT3 MNW‐15‐D1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐2‐Q407 MNW‐15‐D1‐2 10/1/2007 13:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7‐Q407 MNW‐15‐D1‐7 10/1/2007 13:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐12‐Q407 MNW‐15‐D1‐12 10/1/2007 13:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐17‐Q407 MNW‐15‐D1‐17 10/1/2007 13:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐17_070219 MNW‐15‐D1‐17 2/19/2007 13:38 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 MNW‐15‐D1‐12_070219 MNW‐15‐D1‐12 2/19/2007 13:36 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 MNW‐15‐D1‐7_070219 MNW‐15‐D1‐7 2/19/2007 13:34 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 MNW‐15‐D1‐2_070219 MNW‐15‐D1‐2 2/19/2007 13:31 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 F2664 MNW‐15‐D1‐17 8/29/2006 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2663 MNW‐15‐D1‐12 8/29/2006 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2666 MNW‐15‐D1‐7 8/29/2006 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2665 MNW‐15‐D1‐2 8/29/2006 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F1YS1 MNW‐15‐D1‐17 2/7/2006 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F1YS0 MNW‐15‐D1‐12 2/7/2006 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 39 OF 72
011406
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐15 (D1) D1 F1YR9 MNW‐15‐D1‐7 2/7/2006 8:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F1YR8 MNW‐15‐D1‐2 2/7/2006 8:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐15 (D2) 5/10/2020 0:00 unknownMNW‐15 (D2) D2 F6PD1 MNW‐15‐D2‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F5G29 MNW‐15‐D2‐7 2/28/2012 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F3S17 MNW‐15‐D2‐7 2/15/2011 12:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐7‐Q209 MNW‐15‐D2‐7 4/20/2009 14:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐7‐Q408 MNW‐15‐D2‐7 10/6/2008 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2RT4 MNW‐15‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐2‐Q407 MNW‐15‐D2‐2 10/1/2007 13:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐7‐Q407 MNW‐15‐D2‐7 10/1/2007 13:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐12‐Q407 MNW‐15‐D2‐12 10/1/2007 13:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐17‐Q407 MNW‐15‐D2‐17 10/1/2007 13:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐17_070219 MNW‐15‐D2‐17 2/19/2007 14:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 MNW‐15‐D2‐12_070219 MNW‐15‐D2‐12 2/19/2007 13:57 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 MNW‐15‐D2‐7_070319 MNW‐15‐D2‐7 2/19/2007 13:54 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 MNW‐15‐D2‐2_070219 MNW‐15‐D2‐2 2/19/2007 13:52 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 F2668 MNW‐15‐D2‐17 8/29/2006 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2667 MNW‐15‐D2‐12 8/29/2006 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2670 MNW‐15‐D2‐7 8/29/2006 9:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2669 MNW‐15‐D2‐2 8/29/2006 9:50 PDB GW µg/L 0.5 UR 0.5 U 0.5 UR 0.5 U 0.5 URMNW‐15 (D2) D2 F1YS5 MNW‐15‐D2‐17 2/7/2006 9:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F1YS4 MNW‐15‐D2‐12 2/7/2006 8:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F1YS3 MNW‐15‐D2‐7 2/7/2006 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F1YS2 MNW‐15‐D2‐2 2/7/2006 8:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐15 (D3) 5/10/2020 0:00 unknownMNW‐15 (D3) D3 F6PD2 MNW‐15‐D3‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F5G30 MNW‐15‐D3‐7 2/28/2012 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F3S18 MNW‐15‐D3‐7 2/15/2011 12:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7_100201 MNW‐15‐D3‐7 2/1/2010 8:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7‐Q209 MNW‐15‐D3‐7 4/20/2009 14:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7‐Q408 MNW‐15‐D3‐7 10/6/2008 11:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2RT5 MNW‐15‐D3‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐2‐Q407 MNW‐15‐D3‐2 10/1/2007 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7‐Q407 MNW‐15‐D3‐7 10/1/2007 14:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐12‐Q407 MNW‐15‐D3‐12 10/1/2007 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐17‐Q407 MNW‐15‐D3‐17 10/1/2007 14:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐17_070219 MNW‐15‐D3‐17 2/19/2007 14:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D3) D3 MNW‐15‐D3‐12_070219 MNW‐15‐D3‐12 2/19/2007 14:17 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D3) D3 MNW‐15‐D3‐7_070219 MNW‐15‐D3‐7 2/19/2007 14:15 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 40 OF 72
011407
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐15 (D3) D3 MNW‐15‐D3‐2_070219 MNW‐15‐D3‐2 2/19/2007 14:13 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D3) D3 F2672 MNW‐15‐D3‐17 8/29/2006 10:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2671 MNW‐15‐D3‐12 8/29/2006 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2674 MNW‐15‐D3‐7 8/29/2006 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2673 MNW‐15‐D3‐2 8/29/2006 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F1YS9 MNW‐15‐D3‐17 2/7/2006 9:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F1YS8 MNW‐15‐D3‐12 2/7/2006 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F1YS7 MNW‐15‐D3‐7 2/7/2006 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F1YS6 MNW‐15‐D3‐2 2/7/2006 9:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D1) 5/10/2020 0:00 unknownMNW‐16 (D1) D1 MNW‐16‐D1‐12‐022014 MNW‐16‐D1‐12 2/18/2014 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐17‐0813FD MNW‐16‐D1‐17FD 8/12/2013 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐17‐0813 MNW‐16‐D1‐17 8/12/2013 9:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐12‐0813 MNW‐16‐D1‐12 8/12/2013 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐7‐0813 MNW‐16‐D1‐7 8/12/2013 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐2‐0813 MNW‐16‐D1‐2 8/12/2013 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD6 MNW‐16‐D1‐17‐FD 2/12/2013 9:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD4 MNW‐16‐D1‐17 2/12/2013 9:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD3 MNW‐16‐D1‐12 2/12/2013 9:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD7 MNW‐16‐D1‐7 2/12/2013 9:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD5 MNW‐16‐D1‐2 2/12/2013 9:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE7 MNW‐16‐D1‐17 8/20/2012 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE6 MNW‐16‐D1‐12 8/20/2012 10:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE5 MNW‐16‐D1‐7 8/20/2012 10:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE4 MNW‐16‐D1‐2 8/20/2012 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D2) 5/10/2020 0:00 unknownMNW‐16 (D2) D2 MNW‐16‐D2‐12‐022014 MNW‐16‐D2‐12 2/18/2014 8:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐17‐0813 MNW‐16‐D2‐17 8/12/2013 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐12‐0813 MNW‐16‐D2‐12 8/12/2013 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐7‐0813 MNW‐16‐D2‐7 8/12/2013 9:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐2‐0813 MNW‐16‐D2‐2 8/12/2013 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PD9 MNW‐16‐D2‐17 2/12/2013 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PD8 MNW‐16‐D2‐12 2/12/2013 9:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PE1 MNW‐16‐D2‐7 2/12/2013 9:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PE0 MNW‐16‐D2‐2 2/12/2013 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CF1 MNW‐16‐D2‐17 8/20/2012 9:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CH8 MNW‐16‐D2‐12‐FD 8/20/2012 9:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CF0 MNW‐16‐D2‐12 8/20/2012 9:06 PDB GW µg/L 0.5 U 0.043 LJ 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CE9 MNW‐16‐D2‐7 8/20/2012 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CE8 MNW‐16‐D2‐2 8/20/2012 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D3) 5/10/2020 0:00 unknown
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 41 OF 72
011408
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
MNW‐16 (D3) D3 MNW‐16‐D3‐12‐022014 MNW‐16‐D3‐12 2/18/2014 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐17‐0813 MNW‐16‐D3‐17 8/12/2013 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐12‐0813 MNW‐16‐D3‐12 8/12/2013 9:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐7‐0813 MNW‐16‐D3‐7 8/12/2013 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐2‐0813 MNW‐16‐D3‐2 8/12/2013 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE3 MNW‐16‐D3‐17 2/12/2013 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE2 MNW‐16‐D3‐12 2/12/2013 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE5 MNW‐16‐D3‐7 2/12/2013 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE4 MNW‐16‐D3‐2 2/12/2013 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF6 MNW‐16‐D3‐17 8/20/2012 9:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF5 MNW‐16‐D3‐12 8/20/2012 9:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF4 MNW‐16‐D3‐7‐FD 8/20/2012 9:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF3 MNW‐16‐D3‐7 8/20/2012 9:33 PDB GW µg/L 0.5 U 0.030 LJ 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF2 MNW‐16‐D3‐2 8/20/2012 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D4) 5/10/2020 0:00 unknownMNW‐16 (D4) D4 MNW‐16‐D4‐17‐0813FD MNW‐16‐D4‐17FD 8/12/2013 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐17‐0813 MNW‐16‐D4‐17 8/12/2013 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐12‐0813 MNW‐16‐D4‐12 8/12/2013 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐7‐0813 MNW‐16‐D4‐7 8/12/2013 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐2‐0813 MNW‐16‐D4‐2 8/12/2013 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE7 MNW‐16‐D4‐17 2/12/2013 11:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE6 MNW‐16‐D4‐12 2/12/2013 10:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE9 MNW‐16‐D4‐7 2/12/2013 10:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE8 MNW‐16‐D4‐2 2/12/2013 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CG0 MNW‐16‐D4‐17 8/20/2012 8:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CF9 MNW‐16‐D4‐12 8/20/2012 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CF8 MNW‐16‐D4‐7 8/20/2012 8:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CF7 MNW‐16‐D4‐2 8/20/2012 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
Presbyterian unknown 5/10/2020 0:00 unknownPresbyterian unknown Presbyterian NA 1/13/2010 10:30 unknown GW µg/L 0.14 = 0.5 U 0.1 U 0.61 = 0.1 UPresbyterian unknown FGT00 NA 5/4/2000 0:00 OTHER GW µg/L 1 U 1 U 1 U 1 = 1 UPresbyterian unknown FGF62 NA 7/27/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UPresbyterian unknown FFZ71 NA 11/10/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UPresbyterian unknown FFZ72 NA 11/10/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 U
Rutledge Linen unknown 5/10/2020 0:00 unknownRutledge Linen unknown notassigned‐11 NA 3/12/1987 0:00 unknown GW µg/L ND ND ND NDRutledge Linen unknown notassigned‐29 NA 1/22/1987 0:00 unknown GW µg/L T 1 =Rutledge Linen unknown notassigned‐10 NA 1/22/1987 0:00 unknown GW µg/L ND ND ND 1 =Rutledge Linen unknown notassigned‐28 NA 12/30/1986 0:00 unknown GW µg/L T 2 =Rutledge Linen unknown notassigned‐9 NA 12/30/1986 0:00 unknown GW µg/L ND ND ND 2 =
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 42 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐01 (S) NA 5/10/2020 0:00 unknownSFMW‐01 (S) S FQ885 NA 11/12/1997 0:00 unknown GW µg/L 1 = 1 U 1 = 0.7 J 1 USFMW‐01 (S) S FW894 NA 12/11/1996 0:00 unknown GW µg/L 1 = 1 U 2 = 0.8 J 1 USFMW‐01 (S) S FW893 NA 12/11/1996 0:00 unknown GW µg/L 1 = 1 U 1 = 0.9 J 1 USFMW‐01 (S) S FX009 NA 9/2/1993 0:00 unknown GW µg/L 3 = 1 U 4 = 2 = NDSFMW‐01 (S) S FQ927 NA 5/20/1993 0:00 unknown GW µg/L 6 J 10 U 2 J NDSFMW‐01 (S) S 2749 NA 6/1/1990 0:00 unknown GW µg/L 4 = 0.1 U 3.2 = 4.7 = NDSFMW‐01 (S) S OR‐90‐0815 NA 5/31/1990 0:00 unknown GW µg/L 3.4 = T 2.6 = 3.7 =
SFMW‐02 (S) NA 5/10/2020 0:00 unknownSFMW‐02 (S) S FX010 NA 8/31/1993 0:00 unknown GW µg/L 2 = 2 = 3 = 2 = NDSFMW‐02 (S) S FQ933 NA 5/20/1993 0:00 unknown GW µg/L 7 J 3 J 3 J NDSFMW‐02 (S) S 2766 NA 6/1/1990 0:00 unknown GW µg/L 7.1 = 0.25 = 9 = 6.6 = NDSFMW‐02 (S) S OR‐90‐0813 NA 5/31/1990 0:00 unknown GW µg/L 4.1 = T 4.5 = 4.4 =SFMW‐02 (S) S OR‐90‐0814 NA 5/31/1990 0:00 unknown GW µg/L 4.3 = T 4.6 = 4.4 =
SFMW‐03 (S) NA 5/10/2020 0:00 unknownSFMW‐03 (S) S FGF95 NA 8/2/1999 0:00 unknown GW µg/L 1 = 2 = 2 = 2 = 1 USFMW‐03 (S) S FQ882 NA 11/12/1997 0:00 unknown GW µg/L 2 = 3 = 1 = 2 = 1 USFMW‐03 (S) S FW895 NA 12/12/1996 0:00 unknown GW µg/L 1 = 3 = 1 = 2 = 1 USFMW‐03 (S) S FX011 NA 8/31/1993 0:00 unknown GW µg/L 3 = 1 = 3 = 3 = NDSFMW‐03 (S) S FQ926 NA 5/20/1993 0:00 unknown GW µg/L 7 J 10 U 3 J NDSFMW‐03 (S) S 2751 NA 6/1/1990 0:00 unknown GW µg/L 7.2 = 0.4 = 15.3 = 11.1 = NDSFMW‐03 (S) S OR‐90‐0812 NA 5/31/1990 0:00 unknown GW µg/L 4.7 = T 5.5 = 7.6 =
SFMW‐04 (S) NA 5/10/2020 0:00 unknownSFMW‐04 (S) S FX084 NA 5/2/2000 0:00 BAIL GW µg/L 1 = 1 U 1 = 1 = 1 USFMW‐04 (S) S FQ872 NA 11/6/1997 0:00 unknown GW µg/L 1 = 1 U 1 = 1 = 1 USFMW‐04 (S) S FX012 NA 8/31/1993 0:00 unknown GW µg/L 3 = 0.8 J 4 = 2 = NDSFMW‐04 (S) S FQ925 NA 5/20/1993 0:00 unknown GW µg/L ND 6 J 10 U 2 J NDSFMW‐04 (S) S 2752 NA 6/1/1990 0:00 unknown GW µg/L 7.8 = 0.1 U 8 = 6.2 = NDSFMW‐04 (S) S OR‐90‐0809 NA 5/31/1990 0:00 unknown GW µg/L 4.4 = T 5.9 = 4.2 =
SFMW‐05 (S) NA 5/10/2020 0:00 unknownSFMW‐05 (S) S FGF93 NA 8/2/1999 0:00 unknown GW µg/L 1 = 1 U 0.9 LJ 3 = 1 USFMW‐05 (S) S FQ811 NA 11/6/1997 0:00 unknown GW µg/L 2 = 1 U 1 = 3 = 1 USFMW‐05 (S) S FW879 NA 12/9/1996 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = NDSFMW‐05 (S) S FX013 NA 8/31/1993 0:00 unknown GW µg/L 3 = 1 U 3 = 5 = NDSFMW‐05 (S) S FQ930 NA 5/20/1993 0:00 unknown GW µg/L 6 J 10 U 5 J NDSFMW‐05 (S) S FQ929 NA 5/20/1993 0:00 unknown GW µg/L 7 J 10 U 5 J ND
SFMW‐06 (I) NA 5/10/2020 0:00 unknownSFMW‐06 (I) I FGF92 NA 8/2/1999 0:00 unknown GW µg/L 6 = 1 U 4 = 24 = 1 USFMW‐06 (I) I FQ886 NA 11/12/1997 0:00 unknown GW µg/L 8 = 1 U 4 = 34 = 1 USFMW‐06 (I) I FW886 NA 12/11/1996 0:00 unknown GW µg/L 9 = 1 U 5 = 32 D ND
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 43 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐06 (I) I FW887 NA 12/11/1996 0:00 unknown GW µg/L 8 = 1 U 4 = 33 D NDSFMW‐06 (I) I FX014 NA 8/31/1993 0:00 unknown GW µg/L 6 = 1 U 3 = 25 = NDSFMW‐06 (I) I FX019 NA 8/31/1993 0:00 unknown GW µg/L 6 = 1 U 3 = 26 E NDSFMW‐06 (I) I FQ932 NA 5/20/1993 0:00 unknown GW µg/L 9 J 10 U 20 = ND
SFMW‐07 (S) NA 5/10/2020 0:00 unknownSFMW‐07 (S) S FX083 NA 5/2/2000 0:00 BAIL GW µg/L 1 = 1 U 0.9 LJ 0.6 LJ 1 USFMW‐07 (S) S FGG02 NA 8/3/1999 0:00 unknown GW µg/L 1 = 1 U 1 = 0.6 LJ 1 USFMW‐07 (S) S FQ869 NA 11/6/1997 0:00 unknown GW µg/L 0.9 J 1 U 0.7 J 0.5 J 1 USFMW‐07 (S) S FW897 NA 12/12/1996 0:00 unknown GW µg/L 0.8 J 1 U 1 = 0.5 J 1 USFMW‐07 (S) S FX015 NA 8/31/1993 0:00 unknown GW µg/L 2 = 1 U 2 = 0.8 J NDSFMW‐07 (S) S FQ931 NA 5/20/1993 0:00 unknown GW µg/L 5 J 10 U 10 U ND
SFMW‐08 (S) NA 5/10/2020 0:00 unknownSFMW‐08 (S) S FQ864 NA 11/6/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐09 (I1) NA 5/10/2020 0:00 unknownSFMW‐09 (I1) I1 FW591 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 4 = 1 U 2 = 5 = 1 USFMW‐09 (I1) I1 FW561 NA 2/9/2000 0:00 unknown GW µg/L 3 = 1 U 2 = 4 = 1 USFMW‐09 (I1) I1 FGR63 NA 11/2/1999 0:00 unknown GW µg/L 5 = 1 U 5 = 3 = 1 USFMW‐09 (I1) I1 FGF41 NA 7/27/1999 0:00 unknown GW µg/L 3 = 1 U 2 = 4 = 1 USFMW‐09 (I1) I1 FQ868 NA 11/6/1997 0:00 unknown GW µg/L 0.8 J 1 U 1 U 1 = 1 USFMW‐09 (I1) I1 FQ867 NA 11/6/1997 0:00 unknown GW µg/L 0.8 J 1 U 1 U 0.8 J 1 U
SFMW‐10 (I2) 5/10/2020 0:00 unknownSFMW‐10 (I2) I2 SFMW‐10‐I2‐8‐022014 SFMW‐10‐I2‐8 2/17/2014 9:08 PDB GW µg/L 2.2 = 0.5 U 0.8 = 20.3 = 0.5 USFMW‐10 (I2) I2 F6PH7 SFMW‐10‐I2‐2 2/13/2013 0:00 PDB GW µg/L 3.2 = 0.5 U 1.7 = 16 = 0.5 USFMW‐10 (I2) I2 F6PH8 SFMW‐10‐I2‐5 2/13/2013 0:00 PDB GW µg/L 4.2 = 0.5 U 1.9 = 20 = 0.5 USFMW‐10 (I2) I2 F6PH9 SFMW‐10‐I2‐8 2/13/2013 0:00 PDB GW µg/L 4.3 = 0.5 U 1.9 = 21 = 0.5 USFMW‐10 (I2) I2 F6CA9 SFMW‐10‐I2‐5 8/20/2012 11:15 PDB GW µg/L 4.1 = 0.5 U 2.9 = 15 = 0.5 USFMW‐10 (I2) I2 F6CB0 SFMW‐10‐I2‐8 8/20/2012 10:59 PDB GW µg/L 4.7 = 0.5 U 3.3 = 18 = 0.5 USFMW‐10 (I2) I2 F6CA8 SFMW‐10‐I2‐2 8/20/2012 10:56 PDB GW µg/L 5.1 = 0.5 U 6.1 = 8.4 = 0.5 USFMW‐10 (I2) I2 F5G89 SFMW‐10‐I2‐8 2/27/2012 9:13 PDB GW µg/L 3.6 = 0.5 U 2.4 = 12 = 0.5 USFMW‐10 (I2) I2 F5G88 SFMW‐10‐I2‐5 2/27/2012 9:12 PDB GW µg/L 3 = 0.5 U 1.9 = 11 = 0.5 USFMW‐10 (I2) I2 F5G87 SFMW‐10‐I2‐2 2/27/2012 9:10 PDB GW µg/L 4 = 0.5 U 5 = 5.5 = 0.5 USFMW‐10 (I2) I2 F4ED6 SFMW‐10‐I2‐8‐Q311 8/22/2011 13:47 PDB GW µg/L 2.7 LJ 5.0 U 1.4 LJ 8.8 = 2.0 USFMW‐10 (I2) I2 F4ED5 SFMW‐10‐I2‐5‐Q311 8/22/2011 13:46 PDB GW µg/L 4.3 LJ 5.0 U 2.1 LJ 13 = 2.0 USFMW‐10 (I2) I2 F4ED4 SFMW‐10‐I2‐2‐Q311 8/22/2011 13:45 PDB GW µg/L 3.5 LJ 5.0 U 3.4 LJ 6.1 = 2.0 USFMW‐10 (I2) I2 SFMW‐10‐I2‐8‐Q111 SFMW‐10‐I2‐8 3/24/2011 10:50 PDB GW µg/L 2.4 = 0.5 U 1.1 = 6.2 = 0.5 USFMW‐10 (I2) I2 SFMW‐10‐I2‐5‐Q111 SFMW‐10‐I2‐5 3/24/2011 10:45 PDB GW µg/L 2.3 = 0.5 U 1.0 = 6.1 = 0.5 USFMW‐10 (I2) I2 SFMW‐10‐I2‐2‐Q111 SFMW‐10‐I2‐2 3/24/2011 10:40 PDB GW µg/L 1.9 = 0.5 U 0.9 = 3.3 = 0.5 USFMW‐10 (I2) I2 F3LW2 SFMW‐10‐I2‐Q310 8/30/2010 10:33 PDB GW µg/L 2.4 = 0.5 U 1.2 = 6.9 = 0.5 USFMW‐10 (I2) I2 FGF42 NA 7/27/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐10 (I2) I2 FQ865 NA 11/6/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 44 OF 72
011411
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐11 (S) 5/10/2020 0:00 unknownSFMW‐11 (S) S FQ888 NA 11/13/1997 0:00 unknown GW µg/L 0.8 J 1 U 1 = 1 U 1 U
SFMW‐12 (I1) 5/10/2020 0:00 unknownSFMW‐12 (I1) I1 F6PJ0 SFMW‐12‐I1‐2 2/13/2013 0:00 PDB GW µg/L 0.5 = 0.5 U 0.5 U 0.33 LJ 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐2‐Q111 SFMW‐12‐I1‐2 2/14/2011 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐12 (I1) I1 F3LW4 SFMW‐12‐I1‐5‐Q310 8/31/2010 11:40 PDB GW µg/L 0.46 LJ 0.5 U 0.5 U 0.51 = 0.5 USFMW‐12 (I1) I1 F3LW5 SFMW‐12‐I1‐8‐Q310 8/31/2010 11:40 PDB GW µg/L 0.52 = 0.5 U 0.5 U 0.58 = 0.5 USFMW‐12 (I1) I1 F3LW3 SFMW‐12‐I1‐2‐Q310 8/31/2010 11:40 PDB GW µg/L 0.54 = 0.5 U 0.21 LJ 0.61 = 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐8_100201 SFMW‐12‐I1‐8 2/1/2010 9:24 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 = 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐5_100201 SFMW‐12‐I1‐5 2/1/2010 9:23 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 = 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐2_100201 SFMW‐12‐I1‐2 2/1/2010 9:21 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 = 0.5 USFMW‐12 (I1) I1 F3B64 SFMW‐12‐I1‐8 10/26/2009 10:59 PDB GW µg/L 0.54 = 0.5 U 0.5 U 0.49 LJ 0.5 USFMW‐12 (I1) I1 F3B63 SFMW‐12‐I1‐5 10/26/2009 10:54 PDB GW µg/L 0.57 = 0.5 U 0.5 U 0.51 = 0.5 USFMW‐12 (I1) I1 F3B62 SFMW‐12‐I1‐2 10/26/2009 10:51 PDB GW µg/L 0.56 = 0.5 U 0.5 U 0.55 = 0.5 USFMW‐12 (I1) I1 FGF55 NA 7/27/1999 0:00 unknown GW µg/L 1 = 1 U 0.9 J 2 = 1 USFMW‐12 (I1) I1 FQ889 NA 11/13/1997 0:00 unknown GW µg/L 2 = 1 U 1 = 2 = 1 U
SFMW‐13 (I2) 5/10/2020 0:00 unknownSFMW‐13 (I2) I2 F6PJ1 SFMW‐13‐I2‐5 2/13/2013 0:00 PDB GW µg/L 1 = 0.5 U 0.25 LJ 1.2 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐5‐Q111 SFMW‐13‐I2‐5 2/14/2011 12:55 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐8‐Q310 SFMW13 I2‐8 9/23/2010 13:15 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.0 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐5‐Q310 SFMW13 I2‐5 9/23/2010 13:14 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐2‐Q310 SFMW13 I2‐2 9/23/2010 13:13 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.0 = 0.5 USFMW‐13 (I2) I2 F3LW8 SFMW‐13‐I2‐Q310 8/31/2010 10:15 PDB GW µg/L 0.75 = 0.5 U 0.5 U 0.94 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I1‐8_100201 SFMW‐13‐I1‐8 2/1/2010 9:08 PDB GW µg/L 1 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I1‐5_100201 SFMW‐13‐I1‐5 2/1/2010 9:04 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.4 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I1‐2_100201 SFMW‐13‐I1‐2 2/1/2010 9:01 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐13 (I2) I2 F3B67 SFMW‐13‐I2‐8 10/26/2009 10:42 PDB GW µg/L 1 = 0.5 U 0.37 LJ 1 = 0.5 USFMW‐13 (I2) I2 F3B66 SFMW‐13‐I2‐5 10/26/2009 10:39 PDB GW µg/L 0.85 = 0.5 U 0.32 LJ 0.87 = 0.5 USFMW‐13 (I2) I2 F3B65 SFMW‐13‐I2‐2 10/26/2009 10:36 PDB GW µg/L 0.74 = 0.5 U 0.5 U 0.72 = 0.5 USFMW‐13 (I2) I2 FX087 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 2 = 1 U 1 = 3 = 1 USFMW‐13 (I2) I2 FW557 NA 2/9/2000 0:00 unknown GW µg/L 2 = 1 U 0.9 LJ 2 = 1 USFMW‐13 (I2) I2 FGR58 NA 11/2/1999 0:00 unknown GW µg/L 3 = 1 U 3 = 2 = 1 USFMW‐13 (I2) I2 FGF56 NA 7/27/1999 0:00 unknown GW µg/L 2 = 1 U 1 = 4 = 1 USFMW‐13 (I2) I2 FQ891 NA 11/13/1997 0:00 unknown GW µg/L 3 = 1 U 2 = 7 = 1 U
SFMW‐14 (D1) 5/10/2020 0:00 unknownSFMW-14 (D1) D1 SFMW-14-D1-2-0814 SFMW-14-D1-2 8/25/2014 8:27 PDB GW ug/L 1.0 = 0.5 U 0.6 = 18.8 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐022014‐FD SFMW‐14‐D1‐2‐FD 2/17/2014 10:25 PDB GW µg/L 0.7 = 0.5 U 0.5 U 14.8 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐022014 SFMW‐14‐D1‐2 2/17/2014 9:25 PDB GW µg/L 0.8 = 0.5 U 0.5 U 14.8 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐0813 SFMW‐14‐D1‐2 8/13/2013 9:18 PDB GW µg/L 0.9 = 0.5 U 0.5 U 18.3 = 0.5 USFMW‐14 (D1) D1 F6PJ4 SFMW‐14‐D1‐5 2/18/2013 0:00 PDB GW µg/L 0.86 = 0.5 U 0.21 LJ 12 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 45 OF 72
011412
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐14 (D1) D1 F6PJ3 SFMW‐14‐D1‐8 2/18/2013 0:00 PDB GW µg/L 0.88 = 0.5 U 0.26 LJ 12 = 0.5 USFMW‐14 (D1) D1 F6PJ2 SFMW‐14‐D1‐2 2/18/2013 0:00 PDB GW µg/L 0.94 = 0.5 U 0.29 LJ 13 = 0.5 USFMW‐14 (D1) D1 F6CB3 SFMW‐14‐D1‐8 8/20/2012 12:35 PDB GW µg/L 0.75 = 0.062 LJ 0.19 LJ 14 = 0.5 USFMW‐14 (D1) D1 F6CB2 SFMW‐14‐D1‐5 8/20/2012 12:32 PDB GW µg/L 0.82 = 0.5 U 0.14 LJ 16 = 0.5 USFMW‐14 (D1) D1 F6CB1 SFMW‐14‐D1‐2 8/20/2012 12:28 PDB GW µg/L 0.84 = 0.5 U 0.24 LJ 17 = 0.5 USFMW‐14 (D1) D1 F5G46 SFMW‐14‐D1‐8 2/27/2012 10:39 PDB GW µg/L 0.58 = 0.5 U 0.5 U 7.5 = 0.5 USFMW‐14 (D1) D1 F5G45 SFMW‐14‐D1‐5 2/27/2012 10:36 PDB GW µg/L 0.65 = 0.5 U 0.5 U 8.7 = 0.5 USFMW‐14 (D1) D1 F5G44 SFMW‐14‐D1‐2 2/27/2012 10:34 PDB GW µg/L 0.58 = 0.5 U 0.5 U 7.3 = 0.5 USFMW‐14 (D1) D1 F4EE0 SFMW‐14‐D1‐8‐FD‐Q311 8/22/2011 14:33 PDB GW µg/L 5.0 U 5.0 U 5.0 U 7.9 = 2.0 USFMW‐14 (D1) D1 F4ED9 SFMW‐14‐D1‐8‐Q311 8/22/2011 14:32 PDB GW µg/L 5.0 U 5.0 U 5.0 U 8.5 = 2.0 USFMW‐14 (D1) D1 F4ED8 SFMW‐14‐D1‐5‐Q311 8/22/2011 14:31 PDB GW µg/L 5.0 U 5.0 U 5.0 U 6.9 = 2.0 USFMW‐14 (D1) D1 F4ED7 SFMW‐14‐D1‐2‐Q311 8/22/2011 14:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 7.4 = 2.0 USFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐Q111 SFMW‐14‐D1‐2 2/14/2011 9:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4.6 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐5‐Q111 SFMW‐14‐D1‐5 2/14/2011 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4.3 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐8‐Q111 SFMW‐14‐D1‐8 2/14/2011 9:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4.5 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐I1‐Q310‐FD SFMW‐14‐I1‐Q310‐FD 9/9/2010 9:14 PDB GW µg/L 1.0 = 0.5 U 0.5 U 7.7 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐I1‐Q310 SFMW‐14‐I1‐Q310 9/9/2010 9:13 PDB GW µg/L 1.0 = 0.5 U 0.5 U 8.2 = 0.5 USFMW‐14 (D1) D1 FGF54 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐14 (D1) D1 FQ887 NA 11/13/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐15 (S) 5/10/2020 0:00 unknownSFMW‐15 (S) S F2RW1 SFMW‐15‐S‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐15 (S) S FGF84 NA 8/2/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐15 (S) S FEF64 NA 8/4/1998 0:00 unknown GW µg/L 0.3 J 1 U 1 U 1 U 1 USFMW‐15 (S) S 9711055‐1 NA 11/18/1997 0:00 unknown GW µg/L <1 <1 <1 <1 <5SFMW‐15 (S) S FQ899 NA 11/18/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐16 (I1) 5/10/2020 0:00 unknownSFMW‐16 (I1) I1 SFMW‐16‐I1‐8‐022014 SFMW‐16‐I1‐8 2/18/2014 9:33 PDB GW µg/L 0.8 = 0.5 U 0.5 U 5.8 = 0.5 USFMW‐16 (I1) I1 F6PJ5 SFMW‐16‐I1‐2 2/12/2013 0:00 PDB GW µg/L 0.96 = 0.5 U 0.17 LJ 6.5 = 0.5 USFMW‐16 (I1) I1 F6PJ6 SFMW‐16‐I1‐5 2/12/2013 0:00 PDB GW µg/L 0.95 = 0.5 U 0.18 LJ 7.1 = 0.5 USFMW‐16 (I1) I1 F6PJ7 SFMW‐16‐I1‐8 2/12/2013 0:00 PDB GW µg/L 1.5 = 0.5 U 0.31 LJ 8.3 = 0.5 USFMW‐16 (I1) I1 F6CB7 SFMW‐16‐I1‐8 8/20/2012 13:15 PDB GW µg/L 0.97 = 0.5 U 0.18 LJ 9.9 = 0.5 USFMW‐16 (I1) I1 F6CB6 SFMW‐16‐I1‐5 8/20/2012 13:10 PDB GW µg/L 0.86 = 0.5 U 0.16 LJ 9.6 = 0.5 USFMW‐16 (I1) I1 F6CB5 SFMW‐16‐I1‐2‐FD 8/20/2012 13:07 PDB GW µg/L 0.82 = 0.5 U 0.15 LJ 8.9 = 0.5 USFMW‐16 (I1) I1 F6CB4 SFMW‐16‐I1‐2 8/20/2012 13:06 PDB GW µg/L 0.85 = 0.5 U 0.16 LJ 9.1 = 0.5 USFMW‐16 (I1) I1 F5G91 SFMW‐16‐I1‐2‐FD 2/27/2012 11:37 PDB GW µg/L 0.92 = 0.5 U 0.2 LJ 7 = 0.5 USFMW‐16 (I1) I1 F5G93 SFMW‐16‐I1‐8 2/27/2012 10:45 PDB GW µg/L 0.97 = 0.5 U 0.23 LJ 7.6 = 0.5 USFMW‐16 (I1) I1 F5G92 SFMW‐16‐I1‐5 2/27/2012 10:40 PDB GW µg/L 0.85 = 0.5 U 0.19 LJ 6.7 = 0.5 USFMW‐16 (I1) I1 F5G90 SFMW‐16‐I1‐2 2/27/2012 10:37 PDB GW µg/L 0.87 = 0.5 U 0.2 LJ 6.5 = 0.5 USFMW‐16 (I1) I1 F4EE1 SFMW‐16‐I1‐2‐Q311 8/22/2011 8:50 PDB GW µg/L 1.4 LJ 5.0 U 5.0 U 12 = 2.0 USFMW‐16 (I1) I1 F4EE2 SFMW‐16‐I1‐5‐Q311 8/22/2011 8:50 PDB GW µg/L 1.3 LJ 5.0 U 5.0 U 13 = 2.0 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 46 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐16 (I1) I1 F4EE3 SFMW‐16‐I1‐8‐Q311 8/22/2011 8:50 PDB GW µg/L 1.3 LJ 5.0 U 5.0 U 5.0 U 2.0 USFMW‐16 (I1) I1 SFMW‐16‐I1‐8‐Q111‐FD SFMW‐16‐I1‐8 2/14/2011 11:51 PDB GW µg/L 2.9 = 0.5 U 0.9 = 20.3 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐8‐Q111 SFMW‐16‐I1‐8 2/14/2011 10:51 PDB GW µg/L 3 = 0.5 U 0.9 = 20.8 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐5‐Q111 SFMW‐16‐I1‐5 2/14/2011 10:49 PDB GW µg/L 0.9 = 0.5 U 0.5 U 7.1 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐2‐Q111 SFMW‐16‐I1‐2 2/14/2011 10:47 PDB GW µg/L 0.8 = 0.5 U 0.5 U 6.2 = 0.5 USFMW‐16 (I1) I1 F3LR5 SFMW‐16‐I1‐Q310 9/2/2010 9:20 PDB GW µg/L 3.9 = 0.5 U 1.4 = 32 = 0.5 USFMW‐16 (I1) I2 SFMW‐16‐I2‐8_100201 SFMW‐16‐I1‐8 2/1/2010 13:25 PDB GW µg/L 1.1 = 0.5 U 0.5 U 7.4 = 0.5 USFMW‐16 (I1) I2 SFMW‐16‐I2‐5_100201 SFMW‐16‐I1‐5 2/1/2010 13:22 PDB GW µg/L 1 = 0.5 U 0.5 U 6.3 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐2_100201 SFMW‐16‐I1‐2 2/1/2010 13:20 PDB GW µg/L 1.2 = 0.5 U 0.5 U 7.6 = 0.5 USFMW‐16 (I1) I1 F2RW3 SFMW‐16‐I1‐5 4/14/2008 0:00 PDB GW µg/L 0.74 = 0.5 U 0.5 U 3.4 = 0.5 USFMW‐16 (I1) I1 F2RW2 SFMW‐16‐I1‐2 4/14/2008 0:00 PDB GW µg/L 0.82 = 0.5 U 0.19 LJ 4.8 = 0.5 USFMW‐16 (I1) I1 F2RW4 SFMW‐16‐I1‐8 4/14/2008 0:00 PDB GW µg/L 0.95 = 0.5 U 0.5 U 5.6 = 0.5 USFMW‐16 (I1) I1 FGF69 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 USFMW‐16 (I1) I1 FEF75 NA 8/4/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 0.2 J 1 USFMW‐16 (I1) I1 FQ900 NA 11/18/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐17 (I2) 5/10/2020 0:00 unknownSFMW-17 (I2) I2 SFMW-17-I2-8-0814 SFMW-17-I2-8 8/25/2014 9:14 PDB GW ug/L 3.8 = 0.5 U 3.2 = 5.6 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐022014‐FD SFMW‐17‐I2‐8 2/18/2014 10:23 PDB GW µg/L 3.9 = 0.5 U 2.2 = 7.6 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐022014 SFMW‐17‐I2‐8‐FD 2/18/2014 9:23 PDB GW µg/L 3.1 = 0.5 U 1.8 = 3.7 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐0813 SFMW‐17‐I2‐8 8/12/2013 12:37 PDB GW µg/L 5.1 = 0.5 U 2.6 = 23.6 = 0.5 USFMW‐17 (I2) I2 F6PJ9 SFMW‐17‐I2‐8‐FD 2/12/2013 0:00 PDB GW µg/L 5.5 = 0.5 U 2.4 = 20 = 0.5 USFMW‐17 (I2) I2 F6PJ8 SFMW‐17‐I2‐8 2/12/2013 0:00 PDB GW µg/L 6 = 0.5 U 3.1 = 20 = 0.5 USFMW‐17 (I2) I2 F6CB8 SFMW‐17‐I2‐8 8/20/2012 13:43 PDB GW µg/L 7.4 = 0.5 U 6.6 = 16 = 0.5 USFMW‐17 (I2) I2 F5G94 SFMW‐17‐I2‐8 2/27/2012 10:55 PDB GW µg/L 6.1 = 0.5 U 8.7 = 5.7 = 0.5 USFMW‐17 (I2) I2 F4EE5 SFMW‐17‐I2‐8‐FD‐Q311 8/22/2011 9:05 PDB GW µg/L 8.9 = 5.0 U 14 = 13 = 2.0 USFMW‐17 (I2) I2 F4EE4 SFMW‐17‐I2‐8‐Q311 8/22/2011 9:00 PDB GW µg/L 6.9 = 5.0 U 10 = 7.0 = 2.0 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q111 SFMW‐17‐I2‐8 2/14/2011 10:45 PDB GW µg/L 12.8 = 0.5 U 17.5 = 7.3 J 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q310 SFMW‐17‐I2‐8‐Q310 9/7/2010 11:35 PDB GW µg/L 2.5 = 0.5 U 1.5 = 3.4 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8_100201 SFMW‐17‐I2‐8 2/1/2010 13:40 PDB GW µg/L 6 = 0.5 U 5.7 = 9.4 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q209 SFMW‐17‐I2‐8 4/21/2009 8:23 PDB GW µg/L 6.6 J 0.5 UJ 10.9 J 6.1 J 0.5 JSFMW‐17 (I2) I2 F2RW7 SFMW‐17‐I2‐8 4/14/2008 0:00 PDB GW µg/L 3.5 = 0.5 U 1.7 = 20 = 0.5 USFMW‐17 (I2) I2 F2RW5 SFMW‐17‐I2‐2 4/14/2008 0:00 PDB GW µg/L 0.81 = 0.5 U 0.1 LJ 3.2 = 0.5 UJSFMW‐17 (I2) I2 F2RW6 SFMW‐17‐I2‐5 4/14/2008 0:00 PDB GW µg/L 1.1 = 0.5 U 0.5 U 3.5 = 0.5 UJSFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q407 SFMW‐17‐I2‐8 10/1/2007 8:07 PDB GW µg/L 2.8 = 0.5 U 0.8 = 17.6 = 0.5 USFMW‐17 (I2) I2 F1NS0 SFMW‐17‐I2‐8 7/13/2005 8:06 PDB GW µg/L 0.94 = 0.5 U 0.27 LJ 7.4 = 0.5 USFMW‐17 (I2) I2 F1NR9 SFMW‐17‐I2‐5 7/13/2005 8:04 PDB GW µg/L 0.53 = 0.5 U 0.11 LJ 2.8 = 0.28 LJSFMW‐17 (I2) I2 F1NR8 SFMW‐17‐I2‐2 7/13/2005 8:00 PDB GW µg/L 0.52 = 0.5 U 0.1 LJ 2.6 = 0.3 LJSFMW‐17 (I2) I2 F1DM3 SFMW‐17‐I2‐8 4/19/2005 8:40 PDB GW µg/L 0.83 = 0.5 U 0.27 LJ 7.6 = 0.5 USFMW‐17 (I2) I2 F1DM2 SFMW‐17‐I2‐5 4/19/2005 8:38 PDB GW µg/L 0.61 = 0.5 U 0.12 LJ 3.3 = 0.34 LJSFMW‐17 (I2) I2 F1DM1 SFMW‐17‐I2‐2 4/19/2005 8:36 PDB GW µg/L 0.57 = 0.5 U 0.1 LJ 3.1 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 47 OF 72
011414
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐17 (I2) I2 F17K9 SFMW‐17‐I2‐8 11/9/2004 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4 = 0.5 USFMW‐17 (I2) I2 F17K8 SFMW‐17‐I2‐5 11/9/2004 9:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.3 = 0.5 USFMW‐17 (I2) I2 F17K7 SFMW‐17‐I2‐2 11/9/2004 9:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2 = 0.43 LJSFMW‐17 (I2) I2 SFMW17‐020221 NA 2/21/2002 13:55 unknown GW µg/L 1 U 1 U 1 U 5.1 = 1 USFMW‐17 (I2) I2 FGF70 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐17 (I2) I2 FEF79 NA 8/5/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐17 (I2) I2 FQ898 NA 11/18/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐18 (I1) NA 5/10/2020 0:00 unknownSFMW-18 (I1) I1 SFMW-18-I1-8-0814 SFMW-18-I1-8 8/25/2014 10:03 PDB GW ug/L 1.1 = 0.5 U 0.5 U 2.4 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐022014 SFMW‐18‐I1‐8 2/17/2014 11:05 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.8 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐0813FD SFMW‐18‐I1‐8FD 8/12/2013 10:40 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐0813 SFMW‐18‐I1‐8 8/12/2013 9:40 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.4 = 0.5 USFMW‐18 (I1) I1 F6PK0 SFMW‐18‐I1‐8 2/13/2013 0:00 PDB GW µg/L 0.98 = 0.5 U 0.29 LJ 1.7 = 0.5 USFMW‐18 (I1) I1 F6CD1 SFMW‐18‐I1‐8 8/21/2012 9:55 PDB GW µg/L 0.85 = 0.5 U 0.28 LJ 1.4 = 0.5 USFMW‐18 (I1) I1 F5G95 SFMW‐18‐I1‐8 2/27/2012 10:00 PDB GW µg/L 0.86 = 0.5 U 0.31 LJ 1.3 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐Q111 SFMW‐18‐I1‐8 2/14/2011 11:00 PDB GW µg/L 1 = 0.5 U 0.5 U 2.2 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5‐Q111 SFMW‐18‐I1‐5 2/14/2011 10:55 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.6 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2‐Q111‐FD SFMW‐18‐I1‐2 2/14/2011 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2‐Q111 SFMW‐18‐I1‐2 2/14/2011 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐Q310 SFMW‐18‐I1‐8‐Q310 9/7/2010 12:05 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.6 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5‐Q310‐FD SFMW‐18‐I1‐5‐Q310‐FD 9/7/2010 12:00 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.6 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5‐Q310 SFMW‐18‐I1‐5‐Q310 9/7/2010 11:55 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.5 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2‐Q310 SFMW‐18‐I1‐2‐Q310 9/7/2010 11:50 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8_100201 SFMW‐18‐I1‐8 2/1/2010 11:11 PDB GW µg/L 1.2 = 0.5 U 0.5 U 2 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5_100201 SFMW‐18‐I1‐5 2/1/2010 11:09 PDB GW µg/L 1 = 0.5 U 0.5 U 1.9 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2_100201 SFMW‐18‐I1‐2 2/1/2010 11:07 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.4 = 0.5 USFMW‐18 (I1) I1 F3B72 SFMW‐18‐I1‐8 10/26/2009 12:18 PDB GW µg/L 1.1 = 0.5 U 0.44 LJ 1.8 J 0.5 USFMW‐18 (I1) I1 F3B71 SFMW‐18‐I1‐5 10/26/2009 12:13 PDB GW µg/L 0.9 = 0.5 U 0.35 LJ 1.6 = 0.5 USFMW‐18 (I1) I1 F3B69 SFMW‐18‐I1‐2 10/26/2009 12:10 PDB GW µg/L 0.82 = 0.5 U 0.36 LJ 1.3 = 0.5 USFMW‐18 (I1) I1 FW595 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 4 = 1 U 1 = 17 = 1 USFMW‐18 (I1) I1 FW594 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 5 = 1 U 1 = 18 = 1 USFMW‐18 (I1) I1 FGG03 NA 8/3/1999 0:00 unknown GW µg/L 4 = 1 U 2 = 15 = 1 USFMW‐18 (I1) I1 FQ873 NA 11/6/1997 0:00 unknown GW µg/L 4 = 1 U 1 = 18 = 1 U
SFMW‐19 (I2) NA 5/10/2020 0:00 unknownSFMW‐19 (I2) I2 FGG53 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 LJ 10 U 10 U 66 = 10 USFMW‐19 (I2) I2 FFZ90 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 LJ 10 U 10 U 72 = 10 USFMW‐19 (I2) I2 FW569 NA 2/10/2000 0:00 unknown GW µg/L 9 = 1 U 1 = 86 = 1 USFMW‐19 (I2) I2 FW570 NA 2/10/2000 0:00 unknown GW µg/L 9 = 1 U 1 = 90 = 1 USFMW‐19 (I2) I2 FGR76 NA 11/3/1999 0:00 unknown GW µg/L 13 = 1 U 4 = 73 = 1 USFMW‐19 (I2) I2 FGR74 NA 11/3/1999 0:00 unknown GW µg/L 14 = 1 U 4 = 76 = 1 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 48 OF 72
011415
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐19 (I2) I2 FGG06 NA 8/3/1999 0:00 unknown GW µg/L 10 = 1 U 2 = 75 = 1 USFMW‐19 (I2) I2 FQ870 NA 11/6/1997 0:00 unknown GW µg/L 7 = 1 U 0.9 J 36 = 1 USFMW‐19 (I2) I2 FQ851 NA 11/4/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐20 (I1) 5/10/2020 0:00 unknownSFMW-20 (I1) I1 SFMW-20-I1-5-0814 SFMW-20-I1-5 8/25/2014 12:25 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐022014 SFMW‐20‐I1‐5 2/17/2014 8:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐0813 SFMW‐20‐I1‐5 8/13/2013 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐20 (I1) I1 F6PK1 SFMW‐20‐I1‐5 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.16 LJ 0.5 USFMW‐20 (I1) I1 F6CG1 SFMW‐20‐I1‐5 8/20/2012 14:49 PDB GW µg/L 0.5 U 0.037 LJ 0.5 U 0.11 LJ 0.5 USFMW‐20 (I1) I1 F5G96 SFMW‐20‐I1‐5 2/28/2012 12:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 USFMW‐20 (I1) I1 F4EE6 SFMW‐20‐I1‐5‐Q311 8/22/2011 14:25 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐20 (I1) I1 F3S39 SFMW‐20‐I1‐5 2/15/2011 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5_100201 SFMW‐20‐I1‐5 2/1/2010 15:02 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐20 (I1) I1 F3B04 SFMW‐20‐I1‐5 10/26/2009 12:10 PDB GW µg/L 0.43 LJ 0.5 U 0.5 U 0.75 = 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐Q209 SFMW‐20‐I1‐5 4/21/2009 9:20 PDB GW µg/L 0.8 J 0.5 UJ 0.5 UJ 1.1 J 0.5 UJSFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐Q408 SFMW‐20‐I1‐5 10/7/2008 10:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐20 (I1) I1 F2RW8 SFMW‐20‐I1‐5 4/14/2008 0:00 PDB GW µg/L 1.1 = 0.5 U 0.49 LJ 2.3 = 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐Q407 SFMW‐20‐I1‐5 10/2/2007 10:19 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1_070219 SFMW‐20‐I1‐5 2/19/2007 11:53 PDB GW µg/L 1.2 JL 0.5 UJ 0.7 JL 2.6 JL 0.5 UJSFMW‐20 (I1) I1 F2691 SFMW‐20‐I1‐5 8/28/2006 9:55 PDB GW µg/L 0.52 = 0.5 U 0.5 U 1 = 0.5 USFMW‐20 (I1) I1 F1YP2 SFMW‐20‐I1‐5 2/6/2006 13:11 PDB GW µg/L 1.2 = 0.5 U 0.64 = 2.3 = 0.5 USFMW‐20 (I1) I1 F1NT4 SFMW‐20‐I1‐8 7/11/2005 11:58 PDB GW µg/L 0.92 = 0.5 U 0.68 = 3.4 = 0.5 USFMW‐20 (I1) I1 F1NT3 SFMW‐20‐I1‐5 7/11/2005 11:55 PDB GW µg/L 0.92 = 0.5 U 0.69 = 3.4 = 0.5 USFMW‐20 (I1) I1 F1NT2 SFMW‐20‐I1‐2 7/11/2005 11:53 PDB GW µg/L 0.81 = 0.5 U 0.46 LJ 2.2 = 0.5 USFMW‐20 (I1) I1 F1DN7 SFMW‐20‐I1‐8 4/18/2005 14:40 PDB GW µg/L 2.7 = 0.15 LJ 1.4 = 5.2 = 0.17 LJSFMW‐20 (I1) I1 F1DN6 SFMW‐20‐I1‐5 4/18/2005 14:38 PDB GW µg/L 2 = 0.11 LJ 1 = 4.3 = 0.18 LJSFMW‐20 (I1) I1 F1DN5 SFMW‐20‐I1‐2 4/18/2005 14:36 PDB GW µg/L 2.3 = 0.13 LJ 1.1 = 4.8 = 0.17 LJSFMW‐20 (I1) I1 F17W4 SFMW‐20‐I1‐8 11/8/2004 15:20 PDB GW µg/L 1.6 = 0.5 U 0.77 = 3.2 = 0.5 USFMW‐20 (I1) I1 F17W3 SFMW‐20‐I1‐5 11/8/2004 15:15 PDB GW µg/L 1.3 = 0.5 U 0.69 = 2.9 = 0.5 USFMW‐20 (I1) I1 F17W2 SFMW‐20‐I1‐2 11/8/2004 15:10 PDB GW µg/L 1.3 = 0.5 U 0.64 = 2.9 = 0.5 USFMW‐20 (I1) I1 SFMW20‐020305 NA 3/5/2002 13:35 unknown GW µg/L 1.2 = 1 U 1 U 2.3 = 1 USFMW‐20 (I1) I1 FGF81 NA 8/2/1999 0:00 unknown GW µg/L 2 = 1 U 0.9 LJ 4 = 1 USFMW‐20 (I1) I1 FQ849 NA 11/4/1997 0:00 unknown GW µg/L 2 = 1 U 0.8 J 4 = 1 U
SFMW‐21 (I2) NA 5/10/2020 0:00 unknownSFMW-21 (I2) I2 SFMW-21-I2-17-0814 SFMW-21-I2-17 8/25/2014 12:12 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW-21 (I2) I2 SFMW-21-I2-12-0814 SFMW-21-I2-12 8/25/2014 12:08 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐022014 SFMW‐21‐I2‐12 2/17/2014 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐022014 SFMW‐21‐I2‐17 2/17/2014 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐0813 SFMW‐21‐I2‐17 8/13/2013 10:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.6 =SFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐0813 SFMW‐21‐I2‐12 8/13/2013 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 49 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐21 (I2) I2 F6PK3 SFMW‐21‐I2‐17 2/19/2013 9:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F6PK2 SFMW‐21‐I2‐12 2/19/2013 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F6CG4 SFMW‐21‐I2‐17‐FD 8/20/2012 14:44 PDB GW µg/L 0.12 LJ 0.5 U 0.5 U 0.097 LJ 0.5 USFMW‐21 (I2) I2 F6CG3 SFMW‐21‐I2‐17 8/20/2012 14:43 PDB GW µg/L 0.12 LJ 0.5 U 0.5 U 0.080 LJ 0.5 USFMW‐21 (I2) I2 F6CG2 SFMW‐21‐I2‐12 8/20/2012 14:39 PDB GW µg/L 0.12 LJ 0.031 LJ 0.054 LJ 0.10 LJ 0.5 USFMW‐21 (I2) I2 F5G99 SFMW‐21‐12‐17‐FD 2/28/2012 12:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F5G98 SFMW‐21‐I2‐17 2/28/2012 11:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F5G97 SFMW‐21‐I2‐12 2/28/2012 11:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F4EE8 SFMW‐21‐I2‐17‐Q311 8/22/2011 14:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐21 (I2) I2 F4EE7 SFMW‐21‐I2‐12‐Q311 8/22/2011 14:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐21 (I2) I2 F3S41 SFMW‐21‐I2‐17 2/15/2011 11:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐21 (I2) I2 F3S40 SFMW‐21‐I2‐12 2/15/2011 11:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐12_100201 SFMW‐21‐I2‐12 2/1/2010 14:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17_100201 SFMW‐21‐I2‐17 2/1/2010 14:28 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F3B05 SFMW‐21‐I2‐12 10/26/2009 11:51 PDB GW µg/L 0.38 LJ 0.5 U 0.5 U 0.37 LJ 0.5 USFMW‐21 (I2) I2 F3B06 SFMW‐21‐I2‐17 10/26/2009 11:48 PDB GW µg/L 0.78 = 0.5 U 0.34 LJ 0.73 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐Q209 SFMW‐21‐I2‐17 4/21/2009 9:13 PDB GW µg/L 0.9 J 0.5 UJ 0.5 UJ 0.9 J 0.5 UJSFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐Q209 SFMW‐21‐I2‐12 4/21/2009 9:11 PDB GW µg/L 0.6 J 0.5 UJ 0.5 UJ 0.6 J 0.5 UJSFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐Q408 SFMW‐21‐I2‐17 10/7/2008 9:59 PDB GW µg/L 1.2 = 0.5 U 0.5 U 0.9 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐Q408 SFMW‐21‐I2‐12 10/7/2008 9:57 PDB GW µg/L 0.9 = 0.5 U 0.5 U 0.8 = 0.5 USFMW‐21 (I2) I2 F2RW9 SFMW‐21‐I2‐12 4/14/2008 0:00 PDB GW µg/L 1.2 = 0.5 U 0.49 LJ 1.1 = 0.5 USFMW‐21 (I2) I2 F2RX0 SFMW‐21‐I2‐17 4/14/2008 0:00 PDB GW µg/L 1.4 = 0.5 U 0.58 = 1.2 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐Q407 SFMW‐21‐I2‐17 10/1/2007 13:35 PDB GW µg/L 1.7 = 0.5 U 0.8 = 1.6 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐Q407 SFMW‐21‐I2‐12 10/1/2007 13:32 PDB GW µg/L 1.6 = 0.5 U 0.8 = 1.6 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17_070219 SFMW‐21‐I2‐17 2/19/2007 11:42 PDB GW µg/L 1.9 JL 0.5 UJ 1 JL 2.2 JL 0.5 UJSFMW‐21 (I2) I2 SFMW‐21‐I2‐12_070219 SFMW‐21‐I2‐12 2/19/2007 11:38 PDB GW µg/L 1.6 JL 0.5 UJ 0.8 JL 1.8 JL 0.5 UJSFMW‐21 (I2) I2 F2693 SFMW‐21‐I2‐17 8/28/2006 10:15 PDB GW µg/L 1.5 = 0.5 U 0.73 = 1.5 = 0.5 USFMW‐21 (I2) I2 F2692 SFMW‐21‐I2‐12 8/28/2006 10:12 PDB GW µg/L 1.6 = 0.5 U 0.79 = 1.7 = 0.5 USFMW‐21 (I2) I2 F1YP5 SFMW‐21‐I2‐17 2/6/2006 13:05 PDB GW µg/L 2.9 = 0.5 U 1.5 = 3.1 = 0.5 USFMW‐21 (I2) I2 F1YP4 SFMW‐21‐I2‐12 2/6/2006 13:04 PDB GW µg/L 2.6 = 0.5 U 1.3 = 2.8 = 0.5 USFMW‐21 (I2) I2 F1YP3 SFMW‐21‐I2‐7 2/6/2006 13:02 PDB GW µg/L 0.8 = 0.5 U 1.4 = 0.5 U 0.5 USFMW‐21 (I2) I2 F1NT9 SFMW‐21‐I2‐17 7/11/2005 12:20 PDB GW µg/L 2.9 = 0.5 U 2.3 = 4.7 = 0.5 USFMW‐21 (I2) I2 F1NT8 SFMW‐21‐I2‐12 7/11/2005 12:18 PDB GW µg/L 2.4 = 0.5 U 3.3 = 0.99 = 0.76 =SFMW‐21 (I2) I2 F1NT7 SFMW‐21‐I2‐7 7/11/2005 12:15 PDB GW µg/L 2.9 = 0.5 U 2.3 = 4.6 = 0.5 USFMW‐21 (I2) I2 F1NT5 SFMW‐21‐I2‐2 7/11/2005 12:10 PDB GW µg/L 1.3 = 0.5 U 2.5 = 0.41 LJ 0.5 USFMW‐21 (I2) I2 F1DP2 SFMW‐21‐I2‐17 4/18/2005 14:56 PDB GW µg/L 3.6 = 0.5 U 1.8 = 4.3 = 0.26 LJSFMW‐21 (I2) I2 F1DP1 SFMW‐21‐I2‐12 4/18/2005 14:54 PDB GW µg/L 5 = 0.1 LJ 2.8 = 5.9 = 0.5 USFMW‐21 (I2) I2 F1DP0 SFMW‐21‐I2‐7 4/18/2005 14:52 PDB GW µg/L 4 = 0.5 U 3.8 = 0.94 = 0.5 USFMW‐21 (I2) I2 F1DN8 SFMW‐21‐I2‐2 4/18/2005 14:48 PDB GW µg/L 3.6 = 0.5 U 4 = 0.77 = 0.5 USFMW‐21 (I2) I2 F17C5 SFMW‐21‐I2 11/9/2004 9:05 LFS GW µg/L 3.3 = 0.5 U 1.9 = 4.5 J^ 0.51 =SFMW‐21 (I2) I2 F17W9 SFMW‐21‐I2‐17 11/8/2004 15:55 PDB GW µg/L 4 = 0.5 U 2.4 = 5.1 = 0.41 LJ
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 50 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐21 (I2) I2 F17W8 SFMW‐21‐I2‐12 11/8/2004 15:50 PDB GW µg/L 4.2 = 0.5 U 2.3 = 5.2 = 0.5 USFMW‐21 (I2) I2 F17W7 SFMW‐21‐I2‐7 11/8/2004 15:45 PDB GW µg/L 4 = 0.5 U 3.2 = 0.5 U 1.4 =SFMW‐21 (I2) I2 F17W5 SFMW‐21‐I2‐2 11/8/2004 15:40 PDB GW µg/L 3.9 = 0.5 U 4 = 0.5 U 1.7 =SFMW‐21 (I2) I2 SFMW21‐020227 NA 2/27/2002 15:31 unknown GW µg/L 3.7 = 1 U 2.2 = 5.5 = 1 USFMW‐21 (I2) I2 FGS94 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 5 = 1 U 3 = 6 = 1 USFMW‐21 (I2) I2 FW558 NA 2/9/2000 0:00 unknown GW µg/L 5 = 1 U 3 = 6 = 1 USFMW‐21 (I2) I2 FGR67 NA 11/2/1999 0:00 unknown GW µg/L 10 = 1 U 10 = 6 = 1 USFMW‐21 (I2) I2 FGF83 NA 8/2/1999 0:00 unknown GW µg/L 8 = 0.6 LJ 4 = 10 = 1 USFMW‐21 (I2) I2 FQ853 NA 11/4/1997 0:00 unknown GW µg/L 6 = 0.6 J 3 = 9 = 1 U
SFMW‐22 (D1) NA 5/10/2020 0:00 unknownSFMW-22 (D1) D1 SFMW-22-D1-8-0814 SFMW-22-D1-8 8/25/2014 12:38 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐022014 SFMW‐22‐D1‐8 2/17/2014 9:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐022014‐FD SFMW‐22‐D1‐8 2/17/2014 9:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐0813 SFMW‐22‐D1‐8 8/13/2013 11:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 = 0.5 USFMW‐22 (D1) D1 F6PK4 SFMW‐22‐D1‐8 2/19/2013 9:30 PDB GW µg/L 0.21 LJ 0.5 U 0.21 LJ 0.35 LJ 0.5 USFMW‐22 (D1) D1 F6CD0 SFMW‐22‐D1‐8 8/21/2012 10:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 F5GA0 SFMW‐22‐D1‐8 2/28/2012 12:30 PDB GW µg/L 0.34 LJ 0.5 U 0.5 U 0.69 = 0.5 USFMW‐22 (D1) D1 F4EE9 SFMW‐22‐D1‐8‐Q311 8/22/2011 14:05 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.4 LJ 2.0 USFMW‐22 (D1) D1 F3S42 SMFW‐22‐D1‐8 2/15/2011 12:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 F3RM5 SFMW‐22‐D1‐8 12/14/2010 10:22 PDB GW µg/L 0.4 LJ 0.5 U 0.14 LJ 0.84 = 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8_100202 SFMW‐22‐D1‐8 2/2/2010 7:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐22 (D1) D1 F3B07 SMFW‐22‐D1‐8 10/26/2009 12:42 PDB GW µg/L 0.37 LJ 0.5 U 0.5 U 0.66 = 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐Q209 SMFW‐22‐D1‐8 4/21/2009 9:37 PDB GW µg/L 0.6 J 0.5 UJ 0.5 UJ 1.0 J 0.5 UJSFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐Q408 SMFW‐22‐D1‐8 10/7/2008 10:27 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐Q407 SFMW‐22‐D1‐8 10/2/2007 10:38 PDB GW µg/L 1.6 = 0.5 U 0.5 = 3.4 = 0.5 USFMW‐22 (D1) D1 F2694 SFMW‐22‐D1‐8 8/28/2006 10:25 PDB GW µg/L 1.7 = 0.5 U 0.61 = 3.5 = 0.5 USFMW‐22 (D1) D1 F1NW2 SFMW‐22‐D1‐8 7/11/2005 11:10 PDB GW µg/L 2.3 = 0.5 U 1.5 = 5.4 = 0.5 USFMW‐22 (D1) D1 F1NW1 SFMW‐22‐D1‐5 7/11/2005 11:05 PDB GW µg/L 2 = 0.5 U 1.3 = 4.3 = 0.5 USFMW‐22 (D1) D1 F1NW0 SFMW‐22‐D1‐2 7/11/2005 11:00 PDB GW µg/L 2.4 = 0.5 U 1.6 = 5.1 = 0.5 USFMW‐22 (D1) D1 F1DP5 SFMW‐22‐D1‐8 4/19/2005 12:50 PDB GW µg/L 3 = 0.5 U 1.2 = 5.1 = 0.18 LJSFMW‐22 (D1) D1 F1DP4 SFMW‐22‐D1‐5 4/19/2005 12:48 PDB GW µg/L 2.9 = 0.5 U 1.3 = 4.1 = 0.5 USFMW‐22 (D1) D1 F1DP3 SFMW‐22‐D1‐2 4/19/2005 12:46 PDB GW µg/L 2.9 = 0.5 U 1.3 = 3.9 = 0.18 LJSFMW‐22 (D1) D1 F17X2 SFMW‐22‐D1‐8 11/8/2004 14:00 PDB GW µg/L 3.3 = 0.5 U 1.2 = 5.3 = 0.5 USFMW‐22 (D1) D1 F17X1 SFMW‐22‐D1‐5 11/8/2004 13:55 PDB GW µg/L 3.4 = 0.5 U 1.5 = 5 = 0.5 USFMW‐22 (D1) D1 F17X0 SFMW‐22‐D1‐2 11/8/2004 13:50 PDB GW µg/L 2.7 = 0.5 U 1.4 = 3.7 = 0.5 USFMW‐22 (D1) D1 SFMW22‐020305 NA 3/5/2002 15:55 unknown GW µg/L 5.1 = 1 U 2.8 = 8.5 = 1 USFMW‐22 (D1) D1 FW593 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 7 = 1 U 3 = 9 = 1 USFMW‐22 (D1) D1 FGF90 NA 8/2/1999 0:00 unknown GW µg/L 7 = 1 U 4 = 11 = 1 USFMW‐22 (D1) D1 FQ848 NA 11/4/1997 0:00 unknown GW µg/L 7 = 1 U 4 = 11 = 1 U
SFMW‐23 (D2) NA 5/10/2020 0:00 unknown
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 51 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW-23 (D2) D2 SFMW-23-D2-5-0814 SFMW-23-D2-5 8/25/2014 12:30 PDB GW ug/L 3.8 = 0.5 U 0.7 = 10.6 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐022014 SFMW‐23‐D2‐5 2/17/2014 9:03 PDB GW µg/L 1.6 = 0.5 U 0.5 U 4 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐0813 SFMW‐23‐D2‐5 8/13/2013 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 3.7 = 0.5 USFMW‐23 (D2) D2 F6PK5 SFMW‐23‐D2‐5 2/19/2013 9:20 PDB GW µg/L 0.72 = 0.5 U 0.16 LJ 1.7 = 0.5 USFMW‐23 (D2) D2 F6CG6 SFMW‐23‐D2‐5 8/20/2012 14:58 PDB GW µg/L 0.099 LJ 0.19 LJ 0.5 U 0.39 LJ 0.5 USFMW‐23 (D2) D2 F5GA1 SFMW‐23‐D2‐5 2/28/2012 12:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.39 LJ 0.5 USFMW‐23 (D2) D2 F4EF0 SFMW‐23‐D2‐5‐Q311 8/22/2011 14:15 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐23 (D2) D2 F3S43 SFMW‐23‐D2‐5 2/15/2011 11:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5_100201 SFMW‐23‐D2‐5 2/1/2010 14:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 USFMW‐23 (D2) D2 F3B08 SFMW‐23‐D2‐5 10/26/2009 12:26 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 0.74 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐FD‐Q209 SFMW‐23‐D2‐5‐FD 4/21/2009 9:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.0 J 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐Q209 SFMW‐23‐D2‐5 4/21/2009 9:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.0 J 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐Q408 SFMW‐23‐D2‐5 10/7/2008 10:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 USFMW‐23 (D2) D2 F2RX1 SFMW‐23‐D2‐5 4/14/2008 0:00 PDB GW µg/L 0.33 LJ 0.44 LJ 0.5 U 1.5 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐Q407 SFMW‐23‐D2‐5 10/2/2007 10:26 PDB GW µg/L 0.5 U 0.5 = 0.5 U 1.8 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2_070219 SFMW‐23‐D2‐5 2/19/2007 12:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.8 JL 0.5 UJSFMW‐23 (D2) D2 F2695 SFMW‐23‐D2‐5 8/28/2006 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.1 = 0.5 USFMW‐23 (D2) D2 F1YP6 SFMW‐23‐D2‐5 2/6/2006 13:17 PDB GW µg/L 0.93 = 0.5 U 0.5 U 3.8 = 0.5 USFMW‐23 (D2) D2 F1NW5 SFMW‐23‐D2‐8 7/11/2005 11:35 PDB GW µg/L 4.5 = 0.5 U 1.9 = 11 = 0.12 LJSFMW‐23 (D2) D2 F1NW4 SFMW‐23‐D2‐5 7/11/2005 11:33 PDB GW µg/L 5.7 = 0.5 U 2.1 = 18 = 0.16 LJSFMW‐23 (D2) D2 F1NW3 SFMW‐23‐D2‐2 7/11/2005 11:30 PDB GW µg/L 4.1 = 0.5 U 1.9 = 9.1 J 0.11 LJSFMW‐23 (D2) D2 F1D94 SFMW‐23‐D2 4/21/2005 8:05 LFS GW µg/L 5.8 = 0.5 U 5.2 = 6.2 = 0.5 USFMW‐23 (D2) D2 F1DP8 SFMW‐23‐D2‐8 4/19/2005 13:12 PDB GW µg/L 5.3 = 0.5 U 2.5 = 13 = 0.18 LJSFMW‐23 (D2) D2 F1DP7 SFMW‐23‐D2‐5 4/19/2005 13:10 PDB GW µg/L 5.3 = 0.5 U 2.2 = 14 = 0.15 LJSFMW‐23 (D2) D2 F1DP6 SFMW‐23‐D2‐2 4/19/2005 13:08 PDB GW µg/L 4.8 = 0.5 U 2 = 11 = 0.16 LJSFMW‐23 (D2) D2 F17C7 SFMW‐23‐D2 11/8/2004 15:24 LFS GW µg/L 6 = 0.5 U 2.2 = 16 J 0.27 LJSFMW‐23 (D2) D2 F17X5 SFMW‐23‐D2‐8 11/8/2004 14:35 PDB GW µg/L 6.3 = 0.5 U 2.6 = 20 = 0.5 USFMW‐23 (D2) D2 F17X4 SFMW‐23‐D2‐5 11/8/2004 14:30 PDB GW µg/L 6.6 = 0.5 U 2.6 = 22 = 0.5 USFMW‐23 (D2) D2 F17X3 SFMW‐23‐D2‐2 11/8/2004 14:25 PDB GW µg/L 8.1 = 0.5 U 2.5 = 19 J 0.34 LJSFMW‐23 (D2) D2 SFMW23‐020307 NA 3/7/2002 11:00 unknown GW µg/L 6.8 = 1 U 2.9 = 27 = 1 USFMW‐23 (D2) D2 SFMW73‐020307 NA 3/7/2002 11:00 unknown GW µg/L 7.1 = 1 U 3.4 = 27 = 1 USFMW‐23 (D2) D2 FGT02 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 10 = 2 U 3 = 32 = 2 USFMW‐23 (D2) D2 FW568 NA 2/10/2000 0:00 unknown GW µg/L 10 = 1 U 4 = 38 = 1 USFMW‐23 (D2) D2 FGR65 NA 11/3/1999 0:00 unknown GW µg/L 16 = 1 U 12 = 35 = 1 USFMW‐23 (D2) D2 FGR66 NA 11/3/1999 0:00 unknown GW µg/L 16 = 1 U 12 = 39 = 1 USFMW‐23 (D2) D2 FGF87 NA 8/2/1999 0:00 unknown GW µg/L 9 = 1 U 4 = 42 = 1 USFMW‐23 (D2) D2 FGF88 NA 8/2/1999 0:00 unknown GW µg/L 12 = 1 U 5 = 42 = 1 USFMW‐23 (D2) D2 FQ852 NA 11/4/1997 0:00 unknown GW µg/L 9 = 1 U 3 = 35 = 1 U
SFMW‐24 (S) NA 5/10/2020 0:00 unknownSFMW‐24 (S) S 200001473 NA 7/10/2000 0:00 unknown GW µg/L 1.1 = <0.5 U 0.7 = 1.2 = <0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 52 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐24 (S) S 200001474 NA 7/10/2000 0:00 unknown GW µg/L 1.1 = <0.5 U 0.7 = 1.2 = <0.5 USFMW‐24 (S) S FW582 NA 5/1/2000 0:00 BAIL GW µg/L 10 = 5 U 3 LJ 35 = 5 USFMW‐24 (S) S FGF67 NA 7/29/1999 0:00 unknown GW µg/L 2 = 1 U 0.9 LJ 2 = 1 USFMW‐24 (S) S FQ860 NA 11/5/1997 0:00 unknown GW µg/L 2 = 1 U 1 = 2 = 1 U
SFMW‐25 (I1) NA 5/10/2020 0:00 unknownSFMW-25 (I1) I1 SFMW-25-I1-5-0814 SFMW-25-I1-5 8/25/2014 13:19 PDB GW ug/L 3.3 = 0.5 U 0.7 = 7.9 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐022014 SFMW‐25‐I1‐5 2/18/2014 10:18 PDB GW µg/L 2.3 = 0.5 U 0.9 = 4.6 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐0813FD SFMW‐25‐I1‐5FD 8/12/2013 9:26 PDB GW µg/L 3.3 = 0.5 U 0.7 = 8 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐0813 SFMW‐25‐I1‐5 8/12/2013 8:26 PDB GW µg/L 3.2 = 0.5 U 0.7 = 7.7 = 0.5 USFMW‐25 (I1) I1 F6PN3 SFMW‐25‐I1‐5 2/12/2013 13:10 PDB GW µg/L 3.9 = 0.5 U 0.76 = 8.9 = 0.5 USFMW‐25 (I1) I1 F6CC1 SFMW‐25‐I1‐5‐FD 8/21/2012 8:36 PDB GW µg/L 3.4 = 0.5 U 0.62 = 8.5 = 0.5 USFMW‐25 (I1) I1 F6CC0 SFMW‐25‐I1‐5 8/21/2012 8:21 PDB GW µg/L 3.6 = 0.034 LJ 0.65 = 8.7 = 0.5 USFMW‐25 (I1) I1 F5GA3 SFMW‐25‐I1‐5‐FD 2/28/2012 9:00 PDB GW µg/L 3 = 0.5 U 0.57 = 8.2 = 0.5 USFMW‐25 (I1) I1 F5GA2 SFMW‐25‐I1‐5 2/28/2012 9:00 PDB GW µg/L 3 = 0.5 U 0.58 = 9.4 = 0.5 USFMW‐25 (I1) I1 F4EF1 SFMW‐25‐I1‐5‐Q311 8/22/2011 11:05 PDB GW µg/L 5.2 = 5.0 U 5.0 U 14 = 2.0 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q111 SFMW‐25‐I1‐5 2/14/2011 10:00 PDB GW µg/L 3.6 = 0.5 U 0.6 = 11 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q310 SFMW‐25‐I1‐5‐Q310 9/7/2010 8:50 PDB GW µg/L 3.9 = 0.5 U 0.7 = 9.9 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5_100201 SFMW‐25‐I1‐5 2/1/2010 14:45 PDB GW µg/L 4 = 0.5 U 0.8 = 9.6 J 0.5 USFMW‐25 (I1) I1 F3B74 SFMW‐25‐I1‐5 10/26/2009 13:45 PDB GW µg/L 3.7 = 0.5 U 0.79 = 10 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q209 SFMW‐25‐I1‐5 4/20/2009 10:20 PDB GW µg/L 4.6 J 0.5 U 1.1 J 11.8 J 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q408 SFMW‐25‐I1‐5 10/6/2008 12:57 PDB GW µg/L 5.3 = 0.5 U 1.6 = 10.4 = 0.5 USFMW‐25 (I1) I1 F2RX2 SFMW‐25‐I1‐5 4/14/2008 0:00 PDB GW µg/L 6.1 = 0.5 U 2.3 = 13 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q407 SFMW‐25‐I1‐5 10/1/2007 12:20 PDB GW µg/L 5.2 = 0.5 U 1.7 = 11.6 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1_070219 SFMW‐25‐I1‐5 2/19/2007 8:50 PDB GW µg/L 6 JL 0.5 UJ 1.9 JL 15.4 JL 0.5 UJSFMW‐25 (I1) I1 F2696 SFMW‐25‐I1‐5 8/28/2006 11:10 PDB GW µg/L 3.7 = 0.5 U 1 = 10 = 0.5 USFMW‐25 (I1) I1 F1YQ6 SFMW‐25‐I1‐5 2/6/2006 13:51 PDB GW µg/L 6.3 = 0.5 U 1.6 = 17 = 0.5 UJSFMW‐25 (I1) I1 F1NS8 SFMW‐25‐I1‐8 7/12/2005 14:12 PDB GW µg/L 7.3 = 0.5 U 1.8 = 20 J 0.5 USFMW‐25 (I1) I1 F1NS7 SFMW‐25‐I1‐5‐FD 7/12/2005 14:09 PDB GW µg/L 7.4 = 0.5 U 1.8 = 21 = 0.5 USFMW‐25 (I1) I1 F1NS6 SFMW‐25‐I1‐5 7/12/2005 14:08 PDB GW µg/L 0.27 R 0.5 UR 0.5 UR 0.43 R 0.5 URSFMW‐25 (I1) I1 F1NS5 SFMW‐25‐I1‐2 7/12/2005 14:07 PDB GW µg/L 7 = 0.5 U 2 = 20 = 0.5 USFMW‐25 (I1) I1 F1DN1 SFMW‐25‐I1‐8 4/18/2005 11:35 PDB GW µg/L 8.8 J 0.5 U 2.5 J 25 J 0.5 USFMW‐25 (I1) I1 F1DM9 SFMW‐25‐I1‐5 4/18/2005 11:31 PDB GW µg/L 7.7 = 0.5 U 2.3 = 23 = 0.14 LJSFMW‐25 (I1) I1 F1DM8 SFMW‐25‐I1‐2 4/18/2005 11:29 PDB GW µg/L 7.4 = 0.5 U 2.3 = 23 = 0.11 LJSFMW‐25 (I1) I1 F17L4 SFMW‐25‐I1‐8 11/9/2004 14:06 PDB GW µg/L 6.1 = 0.5 U 1.5 = 17 = 0.5 USFMW‐25 (I1) I1 F17L2 SFMW‐25‐I1‐5 11/9/2004 14:02 PDB GW µg/L 6.5 = 0.5 U 1.6 = 18 = 0.5 USFMW‐25 (I1) I1 F17L1 SFMW‐25‐I1‐2 11/9/2004 14:00 PDB GW µg/L 4.9 = 0.5 U 1.2 = 10 = 0.5 USFMW‐25 (I1) I1 SFMW75‐020306 NA 3/6/2002 17:10 unknown GW µg/L 7.9 = 1 U 2.1 = 30 = 1 USFMW‐25 (I1) I1 SFMW25‐020306 NA 3/6/2002 17:10 unknown GW µg/L 8.5 = 1 U 2.1 = 30 = 1 USFMW‐25 (I1) I1 FX092 NA 5/3/2000 0:00 BAIL GW µg/L 10 = 5 U 5 U 34 = 5 USFMW‐25 (I1) I1 FW576 NA 2/1/2000 0:00 unknown GW µg/L 13 = 1 U 3 = 15 = 1 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 53 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐25 (I1) I1 FGR82 NA 11/4/1999 0:00 unknown GW µg/L 17 = 1 U 8 = 47 = 1 USFMW‐25 (I1) I1 FGF74 NA 7/29/1999 0:00 unknown GW µg/L 13 = 1 U 4 = 42 = 1 USFMW‐25 (I1) I1 FGF73 NA 7/29/1999 0:00 unknown GW µg/L 12 = 1 U 4 = 44 = 1 USFMW‐25 (I1) I1 FQ862 NA 11/5/1997 0:00 unknown GW µg/L 13 = 1 U 4 = 54 = 1 U
SFMW‐26 (I2) NA 5/10/2020 0:00 unknownSFMW-26 (I2) I2 SFMW-26-I2-8-0814 SFMW-26-I2-8 8/25/2014 13:09 PDB GW ug/L 1.2 = 0.5 U 0.5 U 2.6 = 0.5 USFMW-26 (I2) I2 SFMW-26-I2-2-0814 SFMW-26-I2-2 8/25/2014 13:08 PDB GW ug/L 1.1 = 0.5 U 0.5 U 2.5 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐022014 SFMW‐26‐I2‐8 2/18/2014 10:30 PDB GW µg/L 1.2 = 0.5 U 0.5 U 2.2 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐022014 SFMW‐26‐I2‐2 2/18/2014 10:25 PDB GW µg/L 0.8 = 0.5 U 0.5 U 0.6 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐0813 SFMW‐26‐I2‐8 8/12/2013 8:53 PDB GW µg/L 1.3 = 0.5 U 0.5 U 2.9 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐0813 SFMW‐26‐I2‐2 8/12/2013 8:51 PDB GW µg/L 1.4 = 0.5 U 0.5 U 2.8 = 0.5 USFMW‐26 (I2) I2 F6PK8 SFMW‐26‐I2‐8 2/13/2013 13:10 PDB GW µg/L 1.5 = 0.13 LJ 0.12 LJ 3.1 = 0.5 USFMW‐26 (I2) I2 F6PK7 SFMW‐26‐I2‐2 2/13/2013 13:00 PDB GW µg/L 1.6 = 0.16 LJ 0.5 U 3.1 = 0.5 USFMW‐26 (I2) I2 F6CC3 SFMW‐26‐I2‐8 8/21/2012 8:32 PDB GW µg/L 0.29 LJ 22 J 0.062 LJ 110 J 0.5 USFMW‐26 (I2) I2 F6CC2 SFMW‐26‐I2‐2 8/21/2012 8:29 PDB GW µg/L 1.6 = 0.17 LJ 0.11 LJ 3.0 = 0.5 USFMW‐26 (I2) I2 F5GA5 SFMW‐26‐I2‐8 2/28/2012 9:15 PDB GW µg/L 1.4 = 0.15 LJ 0.11 LJ 3.7 = 0.5 USFMW‐26 (I2) I2 F5GA4 SFMW‐26‐I2‐2 2/28/2012 9:10 PDB GW µg/L 1.4 = 0.5 U 0.1 LJ 3.1 = 0.5 USFMW‐26 (I2) I2 F4EF3 SFMW‐26‐I2‐8‐Q311 8/22/2011 11:15 PDB GW µg/L 2.5 LJ 5.0 U 5.0 U 5.2 = 2.0 USFMW‐26 (I2) I2 F4EF2 SFMW‐26‐I2‐2‐Q311 8/22/2011 11:10 PDB GW µg/L 2.5 LJ 5.0 U 5.0 U 4.6 LJ 2.0 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q111 SFMW‐26‐I2‐8 2/14/2011 10:15 PDB GW µg/L 1.8 = 0.5 U 0.5 U 4.5 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I1‐2‐Q111 SFMW‐26‐I2‐2 2/14/2011 10:10 PDB GW µg/L 1.7 = 0.5 U 0.5 U 3.8 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q310 SFMW‐26‐I2‐8‐Q310 9/7/2010 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q310 SFMW‐26‐I2‐2‐Q310 9/7/2010 9:55 PDB GW µg/L 2.2 = 0.5 U 0.5 U 4.1 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2_100201 SFMW‐26‐I2‐2 2/1/2010 15:00 PDB GW µg/L 2.6 = 0.5 U 1 = 4 = 0.5 USFMW‐26 (I2) I2 F3B76 SFMW‐26‐I2‐8 10/26/2009 13:31 PDB GW µg/L 2.6 = 0.29 LJ 0.5 U 6.4 = 0.5 USFMW‐26 (I2) I2 F3B75 SFMW‐26‐I2‐2 10/26/2009 13:28 PDB GW µg/L 2.3 = 0.48 LJ 0.5 U 4.7 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q209 SFMW‐26‐I2‐8 4/20/2009 10:10 PDB GW µg/L 3.1 J 0.5 U 0.5 U 7.4 J 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q209 SFMW‐26‐I2‐2 4/20/2009 10:09 PDB GW µg/L 3.2 J 0.5 J 0.5 U 6.0 J 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q408 SFMW‐26‐I2‐2 10/6/2008 11:33 PDB GW µg/L 2.3 = 0.5 U 0.6 = 5 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q408 SFMW‐26‐I2‐8 10/6/2008 10:31 PDB GW µg/L 3.7 = 0.5 U 0.5 U 7.8 = 0.5 USFMW‐26 (I2) I2 F2RX3 SFMW‐26‐I2‐2 4/14/2008 0:00 PDB GW µg/L 4 = 0.5 U 1.5 = 5.5 = 0.5 USFMW‐26 (I2) I2 F2RX5 SFMW‐26‐I2‐8 4/14/2008 0:00 PDB GW µg/L 4.4 = 0.52 = 0.33 LJ 8.4 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q407 SFMW‐26‐I2‐8 10/1/2007 12:30 PDB GW µg/L 4.3 = 0.6 = 0.5 U 9.3 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q407 SFMW‐26‐I2‐2 10/1/2007 12:28 PDB GW µg/L 4.4 = 0.8 = 0.5 U 8.2 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8_070219 SFMW‐26‐I2‐8 2/19/2007 8:38 PDB GW µg/L 5.4 JL 0.5 JL 1.4 JL 9.7 JL 0.5 UJSFMW‐26 (I2) I2 SFMW‐26‐I2‐2_070219 SFMW‐26‐I2‐2 2/19/2007 8:30 PDB GW µg/L 5.5 JL 0.7 JL 0.9 JL 10.2 JL 0.5 UJSFMW‐26 (I2) I2 F2699 SFMW‐26‐I2‐8 8/28/2006 11:03 PDB GW µg/L 4.1 = 0.61 = 0.5 U 9.1 = 0.5 USFMW‐26 (I2) I2 F2697 SFMW‐26‐I2‐2 8/28/2006 10:59 PDB GW µg/L 4.8 = 0.93 = 0.57 = 9.3 = 0.5 USFMW‐26 (I2) I2 F1YQ9 SFMW‐26‐I2‐8 2/6/2006 13:56 PDB GW µg/L 6.2 = 0.95 = 0.7 = 13 = 0.5 USFMW‐26 (I2) I2 F1YQ7 SFMW‐26‐I2‐2 2/6/2006 13:48 PDB GW µg/L 6.4 = 1.3 = 0.52 = 12 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 54 OF 72
011421
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐26 (I2) I2 F1NT1 SFMW‐26‐I2‐8 7/12/2005 13:55 PDB GW µg/L 8.2 = 1.2 = 0.76 = 18 = 0.19 LJSFMW‐26 (I2) I2 F1NT0 SFMW‐26‐I2‐5 7/12/2005 13:53 PDB GW µg/L 7.3 = 1.1 = 0.55 = 13 J 0.14 LJSFMW‐26 (I2) I2 F1NS9 SFMW‐26‐I2‐2 7/12/2005 13:50 PDB GW µg/L 8.8 = 1.5 = 0.92 = 17 = 0.18 LJSFMW‐26 (I2) I2 F1DN4 SFMW‐26‐I2‐8 4/18/2005 11:56 PDB GW µg/L 9.7 = 0.79 = 1.8 = 20 = 0.19 LJSFMW‐26 (I2) I2 F1DN3 SFMW‐26‐I2‐5 4/18/2005 11:54 PDB GW µg/L 7.7 = 0.84 = 0.94 = 15 J 0.14 LJSFMW‐26 (I2) I2 F1DN2 SFMW‐26‐I2‐2 4/18/2005 11:50 PDB GW µg/L 10 = 1.2 = 1 = 20 = 0.17 LJSFMW‐26 (I2) I2 F17L7 SFMW‐26‐I2‐8 11/9/2004 14:20 PDB GW µg/L 8.1 = 0.55 = 0.72 = 19 = 0.5 USFMW‐26 (I2) I2 F17L6 SFMW‐26‐I2‐5 11/9/2004 14:17 PDB GW µg/L 9.2 = 0.9 = 0.64 = 20 J 0.35 LJSFMW‐26 (I2) I2 F17L5 SFMW‐26‐I2‐2 11/9/2004 14:15 PDB GW µg/L 8.8 = 0.65 = 0.48 LJ 16 = 0.5 USFMW‐26 (I2) I2 SFMW26‐020307 NA 3/7/2002 8:30 unknown GW µg/L 8.8 = 1 U 1.4 = 22 = 1 USFMW‐26 (I2) I2 FGG54 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 = 1 U 1 = 23 = 1 USFMW‐26 (I2) I2 FGF75 NA 7/29/1999 0:00 unknown GW µg/L 7 = 1 U 2 = 23 = 1 USFMW‐26 (I2) I2 FQ861 NA 11/5/1997 0:00 unknown GW µg/L 7 = 1 U 2 = 22 = 1 U
SFMW‐27 (I2) NA 5/10/2020 0:00 unknownSFMW-27 (I2) I2 SFMW-27-I2-8-0814 SFMW-27-I2-8 8/25/2014 10:18 PDB GW ug/L 6.1 = 0.5 U 4.3 = 14.5 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐022014 SFMW‐27‐I2‐8 2/17/2014 11:17 PDB GW µg/L 4.9 = 0.5 U 2.5 = 13.4 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐0813 SFMW‐27‐I2‐8 8/12/2013 9:50 PDB GW µg/L 5.4 = 0.5 U 4.4 = 11.3 = 0.5 USFMW‐27 (I2) I2 F6PK9 SFMW‐27‐I2‐2 2/13/2013 0:00 PDB GW µg/L 5.9 = 0.5 U 6.5 = 4.5 = 0.5 USFMW‐27 (I2) I2 F6PL0 SFMW‐27‐I2‐5 2/13/2013 0:00 PDB GW µg/L 5.9 = 0.5 U 4.9 = 9 = 0.5 USFMW‐27 (I2) I2 F6PL1 SFMW‐27‐I2‐8 2/13/2013 0:00 PDB GW µg/L 6.3 = 0.5 U 5.6 = 9.8 = 0.5 USFMW‐27 (I2) I2 F6CC6 SFMW‐27‐I2‐8 8/21/2012 7:36 PDB GW µg/L 4.9 = 0.031 LJ 3.4 = 9.9 = 0.5 USFMW‐27 (I2) I2 F6CC5 SFMW‐27‐I2‐5 8/21/2012 7:33 PDB GW µg/L 4.9 = 0.041 LJ 2.9 = 9.4 = 0.5 USFMW‐27 (I2) I2 F6CC4 SFMW‐27‐I2‐2 8/21/2012 7:30 PDB GW µg/L 1.4 = 0.5 U 0.10 LJ 3.0 J 0.5 USFMW‐27 (I2) I2 F5GA8 SFMW‐27‐I2‐8 2/28/2012 8:55 PDB GW µg/L 4.6 = 0.5 U 3.9 = 9.1 = 0.5 USFMW‐27 (I2) I2 F5GA7 SFMW‐27‐I2‐5 2/28/2012 8:54 PDB GW µg/L 4.4 = 0.5 U 3.5 = 9.4 = 0.5 USFMW‐27 (I2) I2 F5GA6 SFMW‐27‐I2‐2 2/28/2012 8:53 PDB GW µg/L 5.3 = 0.5 U 4.7 = 9.5 = 0.5 USFMW‐27 (I2) I2 F4EF6 SFMW‐27‐I2‐8‐Q311 8/23/2011 8:13 PDB GW µg/L 6.7 = 5.0 U 4.7 LJ 13 = 2.0 USFMW‐27 (I2) I2 F4EF5 SFMW‐27‐I2‐5‐Q311 8/23/2011 8:10 PDB GW µg/L 9.3 = 5.0 U 6.6 = 17 = 2.0 USFMW‐27 (I2) I2 F4EF4 SFMW‐27‐I2‐2‐Q311 8/23/2011 8:07 PDB GW µg/L 7.9 = 5.0 U 5.8 = 13 = 2.0 USFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐Q111 SFMW‐27‐I2‐8 2/14/2011 13:52 PDB GW µg/L 6.4 = 0.5 U 5.3 = 8.4 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐5‐Q111 SFMW‐27‐I2‐5 2/14/2011 13:50 PDB GW µg/L 7.1 = 0.5 U 4.8 = 7.2 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐2‐Q111 SFMW‐27‐I2‐2 2/14/2011 13:48 PDB GW µg/L 6.9 = 0.5 U 4.7 = 6.6 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐Q310 SFMW‐27‐I2‐8‐Q310 9/9/2010 9:54 PDB GW µg/L 4.4 = 0.5 U 0.5 U 13.7 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐5‐Q310 SFMW‐27‐I2‐5‐Q310 9/9/2010 9:52 PDB GW µg/L 3.9 = 0.5 U 0.5 U 8.0 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐2‐Q310 SFMW‐27‐I2‐2‐Q310 9/9/2010 9:50 PDB GW µg/L 3.2 = 0.5 U 0.5 U 5.7 = 0.5 USFMW‐27 (I2) I2 FGS84 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 9 = 1 U 1 = 22 = 1 USFMW‐27 (I2) I2 FW565 NA 2/10/2000 0:00 unknown GW µg/L 9 = 1 U 1 = 23 = 1 USFMW‐27 (I2) I2 FGR79 NA 11/4/1999 0:00 unknown GW µg/L 11 = 1 U 3 = 20 = 1 USFMW‐27 (I2) I2 FGG04 NA 8/3/1999 0:00 unknown GW µg/L 10 = 1 U 2 = 32 = 1 USFMW‐27 (I2) I2 FGG05 NA 8/3/1999 0:00 unknown GW µg/L 10 = 1 U 2 = 33 = 1 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 55 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐27 (I2) I2 FEF66 NA 7/30/1998 0:00 unknown GW µg/L 9 = 1 U 2 = 46 = 1 USFMW‐28 (I2) NA 5/10/2020 0:00 unknown
SFMW‐28 (I2) I2 SFMW‐28‐I2‐8‐022014 SFMW‐28‐I2‐8 2/18/2014 11:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐022014 SFMW‐28‐I2‐5 2/18/2014 11:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐2‐022014 SFMW‐28‐I2‐2 2/18/2014 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐8‐0813 SFMW‐28‐I2‐8 8/12/2013 12:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐0813 SFMW‐28‐I2‐5 8/12/2013 12:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐2‐0813 SFMW‐28‐I2‐2 8/12/2013 12:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6PL4 SFMW‐28‐I2‐8 2/13/2013 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6PL3 SFMW‐28‐I2‐5 2/13/2013 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6PL2 SFMW‐28‐I2‐2 2/13/2013 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6CC9 SFMW‐28‐I2‐8 8/21/2012 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6CC8 SFMW‐28‐I2‐5 8/21/2012 9:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6CC7 SFMW‐28‐I2‐2 8/21/2012 9:01 PDB GW µg/L 5.1 = 0.5 U 3.1 = 10 = 0.5 USFMW‐28 (I2) I2 F4EG0 SFMW‐28‐I2‐8‐FD‐Q311 8/22/2011 10:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 F4EF9 SFMW‐28‐I2‐8‐Q311 8/22/2011 10:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 F4EF8 SFMW‐28‐I2‐5‐Q311 8/22/2011 10:25 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 F4EF7 SFMW‐28‐I2‐2‐Q311 8/22/2011 10:20 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐Q111 SFMW‐28‐I2‐5 2/14/2011 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐8‐Q310 SFMW‐28‐I2‐8‐Q310 9/7/2010 12:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐Q310 SFMW‐28‐I2‐5‐Q310 9/7/2010 12:41 PDB GW µg/L 2.3 = 0.5 U 0.5 U 5.2 = 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐2‐Q310 SFMW‐28‐I2‐2‐Q310 9/7/2010 12:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F3B33 SFMW‐28‐I2‐2 10/27/2009 9:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F3B35 SFMW‐28‐I2‐8 10/26/2009 10:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F3B34 SFMW‐28‐I2‐5 10/26/2009 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 FW592 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 7 = 1 = 1 U 10 = 1 USFMW‐28 (I2) I2 FW566 NA 2/10/2000 0:00 unknown GW µg/L 6 = 1 = 1 U 9 = 1 USFMW‐28 (I2) I2 FGR73 NA 11/3/1999 0:00 unknown GW µg/L 11 = 1 = 0.9 LJ 11 = 1 USFMW‐28 (I2) I2 FGF48 NA 7/28/1999 0:00 unknown GW µg/L 10 = 2 = 1 U 16 = 1 USFMW‐28 (I2) I2 FEF67 NA 7/30/1998 0:00 unknown GW µg/L 13 = 2 = 1 U 21 = 1 U
SFMW‐29 (I2) 5/10/2020 0:00 unknownSFMW‐29 (I2) I1 SFMW‐29‐I1‐5‐Q209 SFMW‐29‐I1‐5 4/21/2009 7:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I1 SFMW‐29‐I1‐5‐Q407 SFMW‐29‐I1‐5 10/1/2007 10:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1NS4 SFMW‐29‐I2‐8 7/13/2005 8:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1NS2 SFMW‐29‐I2‐2 7/13/2005 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1NS3 SFMW‐29‐I2‐5 7/13/2005 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1DM7 SFMW‐29‐I2‐8 4/18/2005 13:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1DM6 SFMW‐29‐I2‐5 4/18/2005 13:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1DM5 SFMW‐29‐I2‐2 4/18/2005 13:39 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 USFMW‐29 (I2) I2 F17M0 SFMW‐29‐I2‐8 11/9/2004 11:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 56 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐29 (I2) I2 F17L9 SFMW‐29‐I2‐5 11/9/2004 11:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.33 LJ 0.5 USFMW‐29 (I2) I2 F17L8 SFMW‐29‐I2‐2 11/9/2004 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 SFMW29‐020221 NA 2/21/2002 16:13 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FX094 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FW564 NA 2/10/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FGR62 NA 11/2/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FGF49 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FEF68 NA 7/30/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐30 (I2) NA 5/10/2020 0:00 unknownSFMW‐30 (I2) I2 FGF50 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐30 (I2) I2 FEF72 NA 7/28/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐31 (I2) 5/10/2020 0:00 unknownSFMW‐31 (I2) I2 F6PL7 SFMW‐31‐I2‐8 2/19/2013 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 USFMW‐31 (I2) I2 F6PL6 SFMW‐31‐I2‐5 2/19/2013 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 USFMW‐31 (I2) I2 F6PL5 SFMW‐31‐I2‐2 2/19/2013 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 USFMW‐31 (I2) I2 F3S29 SFMW‐31‐I2‐8 2/15/2011 14:20 PDB GW µg/L 0.25 LJ 0.5 U 0.5 U 0.76 J 0.5 USFMW‐31 (I2) I2 F3S28 SFMW‐31‐I2‐5 2/15/2011 14:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐31 (I2) I2 F3S27 SFMW‐31‐I2‐2 2/15/2011 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐31 (I2) I2 F3LQ0 SFMW‐31‐I2‐8‐Q310 9/2/2010 13:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.44 LJ 0.5 USFMW‐31 (I2) I2 F3LP9 SFMW‐31‐I2‐5‐Q310 9/2/2010 13:35 PDB GW µg/L 0.21 LJ 0.5 U 0.5 U 0.47 LJ 0.5 USFMW‐31 (I2) I2 F3LP8 SFMW‐31‐I2‐2‐Q310 9/2/2010 13:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.44 LJ 0.5 USFMW‐31 (I2) I2 F3B12 SFMW‐31‐I2‐8 10/26/2009 14:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐31 (I2) I2 F3B11 SFMW‐31‐I2‐5 10/26/2009 13:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐31 (I2) I2 F3B10 SFMW‐31‐I2‐2 10/26/2009 13:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐31 (I2) I2 FX093 NA 5/3/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐31 (I2) I2 FGF51 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐31 (I2) I2 FX079 NA 7/27/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐32 (I2) NA 5/10/2020 0:00 unknownSFMW‐32 (I2) I2 F6PL8 SFMW‐32‐I2‐5 2/18/2013 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q111 SFMW‐32‐I2‐5 2/14/2011 12:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q209 SFMW‐32‐I2‐5 4/21/2009 11:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q408 SFMW‐32‐I2‐5 10/7/2008 9:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q407 SFMW‐32‐I2‐5 10/1/2007 8:52 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.8 = 0.5 USFMW‐32 (I2) I2 F26A0 SFMW‐32‐I2‐5 8/28/2006 11:30 PDB GW µg/L 0.73 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐32 (I2) I2 F1NY1 SFMW‐32‐I2‐8 7/11/2005 10:05 PDB GW µg/L 1 = 0.5 U 0.21 LJ 1.9 = 0.11 LJSFMW‐32 (I2) I2 F1NY0 SFMW‐32‐I2‐5 7/11/2005 10:00 PDB GW µg/L 1 = 0.5 U 0.26 LJ 1.7 = 0.1 LJSFMW‐32 (I2) I2 F1NX9 SFMW‐32‐I2‐2 7/11/2005 9:55 PDB GW µg/L 1.3 = 0.5 U 0.26 LJ 2.1 = 0.12 LJSFMW‐32 (I2) I2 F1DR4 SFMW‐32‐I2‐8 4/20/2005 8:35 PDB GW µg/L 1 = 0.5 U 0.24 LJ 1.7 = 0.5 USFMW‐32 (I2) I2 F1DR3 SFMW‐32‐I2‐5 4/20/2005 8:32 PDB GW µg/L 1.1 = 0.5 U 0.24 LJ 1.7 = 0.5 USFMW‐32 (I2) I2 F1DR2 SFMW‐32‐I2‐2 4/20/2005 8:30 PDB GW µg/L 0.98 = 0.5 U 0.27 LJ 1.6 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 57 OF 72
011424
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐32 (I2) I2 F17C8 SFMW‐32‐I2 11/15/2004 14:45 LFS GW µg/L 1.7 = 0.5 U 0.32 LJ 2.7 = 0.5 USFMW‐32 (I2) I2 F17X8 SFMW‐32‐I2‐8 11/8/2004 11:45 PDB GW µg/L 0.95 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐32 (I2) I2 F17X7 SFMW‐32‐I2‐5 11/8/2004 11:40 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐32 (I2) I2 F17X6 SFMW‐32‐I2‐2 11/8/2004 11:35 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐32 (I2) I2 SFMW32‐020222 NA 2/22/2002 11:27 unknown GW µg/L 1.4 = 1 U 1 U 1.2 = 1 USFMW‐32 (I2) I2 FFZ91 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 2 = 1 U 1 U 1 = 1 USFMW‐32 (I2) I2 FW546 NA 2/7/2000 0:00 unknown GW µg/L 3 = 1 U 0.8 LJ 4 = 1 USFMW‐32 (I2) I2 FGR57 NA 11/1/1999 0:00 unknown GW µg/L 2 = 1 U 1 = 1 = 1 USFMW‐32 (I2) I2 FGF52 NA 7/28/1999 0:00 unknown GW µg/L 1 = 1 U 1 U 2 = 1 USFMW‐32 (I2) I2 FX080 NA 7/27/1998 0:00 unknown GW µg/L 1 = 1 U 0.3 J 2 = 1 U
SFMW‐33 (D2) NA 5/10/2020 0:00 unknownSFMW‐33 (D2) D2 F6PM0 SFMW‐33‐D2‐5‐FD 2/13/2013 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F6PL9 SFMW‐33‐D2‐5 2/13/2013 13:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F6CH6 SFMW‐33‐D2‐5 8/22/2012 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F3S46 SFMW‐33‐D2‐5 2/15/2011 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW‐33‐D2‐5‐Q209 SFMW‐33‐D2‐5 4/20/2009 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW‐33‐D2‐5‐Q408 SFMW‐33‐D2‐5 10/7/2008 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW‐33‐D2‐5‐Q407 SFMW‐33‐D2‐5 10/1/2007 12:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F26A1 SFMW‐33‐D2‐5 8/28/2006 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1NX2 SFMW‐33‐D2‐8 7/12/2005 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1NX1 SFMW‐33‐D2‐5 7/12/2005 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1NW9 SFMW‐33‐D2‐2 7/12/2005 9:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1DQ5 SFMW‐33‐D2‐8 4/19/2005 11:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1DQ4 SFMW‐33‐D2‐5 4/19/2005 11:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1DQ2 SFMW‐33‐D2‐2 4/19/2005 11:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F17C9 SFMW‐33‐D2 11/15/2004 9:15 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.16 LJ 0.5 USFMW‐33 (D2) D2 F17Y3 SFMW‐33‐D2‐8 11/9/2004 11:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F17Y2 SFMW‐33‐D2‐5 11/9/2004 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F17Y0 SFMW‐33‐D2‐2 11/9/2004 11:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW33‐020227 NA 2/27/2002 11:17 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐33 (D2) D2 FGS90 NA 5/1/2000 0:00 GRN‐PUMP DUKE GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐33 (D2) D2 FGF60 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐33 (D2) D2 FEF70 NA 7/30/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐34 (D4) NA 5/10/2020 0:00 unknownSFMW‐34 (D4) D4 FGF65 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐34 (D4) D4 FEF69 NA 7/29/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐35 (D3) NA 5/10/2020 0:00 unknownSFMW-35 (D3) D3 SFMW-35-D3-5-0814 SFMW-35-D3-5 8/25/2014 12:00 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐022014 SFMW‐35‐D3‐5 2/17/2014 9:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐0813 SFMW‐35‐D3‐5 8/13/2013 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 58 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐35 (D3) D3 F6PM1 SFMW‐35‐D3‐5 2/19/2013 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F6CG7 SFMW‐35‐D3‐5 8/20/2012 14:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F5GA9 SFMW‐35‐D3‐5 2/28/2012 11:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F3S48 SFMW‐35‐D3‐5 2/15/2011 11:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F3S47 SFMW‐35‐D3‐5 2/15/2011 11:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5_100201 SFMW‐35‐D3‐5 2/1/2010 14:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F3B13 SFMW‐35‐D3‐5 10/26/2009 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐Q209 SFMW‐35‐D3‐5 4/21/2009 9:08 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐Q408 SFMW‐35‐D3‐5 10/7/2008 10:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐Q407 SFMW‐35‐D3‐5 10/1/2007 13:23 PDB GW µg/L 0.7 = 0.5 U 0.5 U 2.3 = 0.5 USFMW‐35 (D3) D3 F26A2 SFMW‐35‐D3‐5 8/28/2006 13:30 PDB GW µg/L 0.76 = 0.5 U 0.5 U 2.8 = 0.5 USFMW‐35 (D3) D3 F1NW7 SFMW‐35‐D3‐5 7/11/2005 14:10 PDB GW µg/L 0.18 LJ 0.5 U 0.5 U 0.72 = 0.5 USFMW‐35 (D3) D3 F1NW8 SFMW‐35‐D3‐8 7/11/2005 14:10 PDB GW µg/L 0.18 LJ 0.5 U 0.5 U 0.99 = 0.5 USFMW‐35 (D3) D3 F1NW6 SFMW‐35‐D3‐2 7/11/2005 14:05 PDB GW µg/L 0.17 LJ 0.5 U 0.5 U 0.82 = 0.5 USFMW‐35 (D3) D3 F1DQ1 SFMW‐35‐D3‐8 4/18/2005 15:45 PDB GW µg/L 0.55 = 0.5 U 0.17 LJ 1.8 = 0.5 USFMW‐35 (D3) D3 F1DQ0 SFMW‐35‐D3‐5 4/18/2005 15:43 PDB GW µg/L 0.42 LJ 0.5 U 0.12 LJ 1.2 = 0.5 USFMW‐35 (D3) D3 F1DP9 SFMW‐35‐D3‐2 4/18/2005 15:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.56 = 0.5 USFMW‐35 (D3) D3 F17Y6 SFMW‐35‐D3‐8 11/9/2004 8:25 PDB GW µg/L 0.77 = 0.5 U 0.5 U 2.3 J 0.5 USFMW‐35 (D3) D3 F17Y5 SFMW‐35‐D3‐5 11/9/2004 8:20 PDB GW µg/L 0.87 = 0.5 U 0.21 LJ 2.7 = 0.5 USFMW‐35 (D3) D3 F17Y4 SFMW‐35‐D3‐2 11/9/2004 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.37 LJ 0.5 USFMW‐35 (D3) D3 SFMW35‐020227 NA 2/27/2002 14:49 unknown GW µg/L 1 U 1 U 1 U 3.2 = 1 USFMW‐35 (D3) D3 FW585 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 0.6 LJ 0.9 LJ 1 U 2 = 1 USFMW‐35 (D3) D3 FW559 NA 2/9/2000 0:00 unknown GW µg/L 1 U 0.8 LJ 1 U 2 = 1 USFMW‐35 (D3) D3 FGR68 NA 11/2/1999 0:00 unknown GW µg/L 0.7 LJ 0.6 LJ 1 U 2 = 1 USFMW‐35 (D3) D3 FGF82 NA 8/2/1999 0:00 unknown GW µg/L 0.6 LJ 1 = 1 U 3 = 1 USFMW‐35 (D3) D3 FQ714 NA 7/27/1998 0:00 unknown GW µg/L 0.7 J 1 = 1 U 3 = 1 USFMW‐35 (D3) D3 FX082 NA 7/27/1998 0:00 unknown GW µg/L 0.7 J 1 = 1 U 3 = 1 U
SFMW‐36 (D4) NA 5/10/2020 0:00 unknownSFMW‐36 (D4) D4 FGF94 NA 8/2/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐36 (D4) D4 FQ723 NA 7/28/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐37 (I2) 5/10/2020 0:00 unknownSFMW‐37 (I2) I2 SFMW‐37‐I2‐5‐022014 SFMW‐37‐I2‐5 2/17/2014 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F6PM2 SFMW‐37‐I2‐5 2/19/2013 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F5GB2 SFMW‐37‐I2‐8 2/27/2012 13:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F5GB1 SFMW‐37‐I2‐5 2/27/2012 13:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F5GB0 SFMW‐37‐I2‐2 2/27/2012 13:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F4EG3 SFMW‐37‐I2‐8‐Q311 8/23/2011 8:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐37 (I2) I2 F4EG2 SFMW‐37‐I2‐5‐Q311 8/23/2011 8:33 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐37 (I2) I2 F4EG1 SFMW‐37‐I2‐2‐Q311 8/23/2011 8:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐37 (I2) I2 SFMW‐37‐I2‐8‐Q111 SFMW‐37‐I2‐8 2/16/2011 12:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 59 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐37 (I2) I2 SFMW‐37‐I2‐5‐Q111 SFMW‐37‐I2‐5 2/16/2011 12:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 SFMW‐37‐I2‐2‐Q111 SFMW‐37‐I2‐2 2/16/2011 12:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 FGS92 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 2 = 1 U 0.6 LJ 2 = 1 USFMW‐37 (I2) I2 FGF53 NA 7/28/1999 0:00 unknown GW µg/L 2 = 1 U 0.8 LJ 3 = 1 USFMW‐37 (I2) I2 FEF77 NA 8/4/1998 0:00 unknown GW µg/L 2 = 1 U 0.8 J 3 = 0.3 JSFMW‐37 (I2) I2 FEF76 NA 8/4/1998 0:00 unknown GW µg/L 2 = 1 U 0.8 J 3 = 1 U
SFMW‐38 (D1) NA 5/10/2020 0:00 unknownSFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐022014 SFMW‐38‐D1‐5 2/18/2014 12:42 PDB GW µg/L 2.7 = 0.5 U 1 = 2.4 = 0.5 USFMW‐38 (D1) D1 F6PM4 SFMW‐38‐D1‐5‐FD 2/18/2013 10:15 PDB GW µg/L 2.9 = 0.5 U 1 = 2.3 = 0.5 USFMW‐38 (D1) D1 F6PM3 SFMW‐38‐D1‐5 2/18/2013 10:10 PDB GW µg/L 3.2 = 0.5 U 1.1 = 2.5 = 0.5 USFMW‐38 (D1) D1 F5G47 SFMW‐38‐D1‐5 2/28/2012 9:12 PDB GW µg/L 2.3 = 0.5 U 1.5 = 0.38 LJ 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q111 SFMW‐38‐D1‐5 2/14/2011 13:03 PDB GW µg/L 3.6 = 0.5 U 3.2 = 0.5 U 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5_100202 SFMW‐38‐D1‐5 2/2/2010 8:30 PDB GW µg/L 3.2 = 0.5 U 1.9 = 1.9 = 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q209 SFMW‐38‐D1‐5 4/21/2009 11:10 PDB GW µg/L 4.3 J 0.5 UJ 2.9 J 1.4 J 0.5 UJSFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q408 SFMW‐38‐D1‐5 10/7/2008 9:24 PDB GW µg/L 4.1 = 0.5 U 2 = 1.8 = 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q407 SFMW‐38‐D1‐5 10/1/2007 8:44 PDB GW µg/L 5 = 0.5 U 3.5 = 0.7 = 0.5 USFMW‐38 (D1) D1 F26A3 SFMW‐38‐D1‐5 8/28/2006 11:45 PDB GW µg/L 4.4 = 0.5 U 1.8 = 1.2 = 0.5 USFMW‐38 (D1) D1 F1NY5 SFMW‐38‐D1‐8 7/11/2005 10:25 PDB GW µg/L 4.6 = 0.5 U 1.4 = 3.6 = 0.2 LJSFMW‐38 (D1) D1 F1NY4 SFMW‐38‐D1‐5 7/11/2005 10:20 PDB GW µg/L 4.7 = 0.5 U 1.4 = 3.9 = 0.2 LJSFMW‐38 (D1) D1 F1NY3 SFMW‐38‐D1‐2 7/11/2005 10:15 PDB GW µg/L 4.9 = 0.5 U 1.5 = 3.7 = 0.5 USFMW‐38 (D1) D1 F1DR8 SFMW‐38‐D1‐8 4/20/2005 9:04 PDB GW µg/L 4.7 = 0.5 U 1.4 = 3.4 = 0.5 USFMW‐38 (D1) D1 F1DR7 SFMW‐38‐D1‐5 4/20/2005 9:02 PDB GW µg/L 4.4 = 0.5 U 1.3 = 3 = 0.24 LJSFMW‐38 (D1) D1 F1DR6 SFMW‐38‐D1‐2 4/20/2005 9:00 PDB GW µg/L 4.5 = 0.5 U 1.4 = 3 = 0.5 USFMW‐38 (D1) D1 F17Y9 SFMW‐38‐D1‐8 11/8/2004 12:20 PDB GW µg/L 6.1 = 0.5 U 2 = 4 = 0.5 USFMW‐38 (D1) D1 F17Y8 SFMW‐38‐D1‐5 11/8/2004 12:15 PDB GW µg/L 5.4 = 0.5 U 1.6 = 1.7 = 0.5 USFMW‐38 (D1) D1 F17Y7 SFMW‐38‐D1‐2 11/8/2004 12:10 PDB GW µg/L 6.9 = 0.5 U 0.91 = 2.8 = 0.5 USFMW‐38 (D1) D1 SFMW38‐020301 NA 3/1/2002 11:30 unknown GW µg/L 7.2 = 1 U 2.4 = 4.6 = 1 USFMW‐38 (D1) D1 FW584 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 = 1 U 2 = 3 = 1 USFMW‐38 (D1) D1 FW545 NA 2/7/2000 0:00 unknown GW µg/L 8 = 1 U 2 = 4 = 1 U
SFMW‐39 (D2) NA 5/10/2020 0:00 unknownSFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐022014 SFMW‐39‐D2‐8 2/18/2014 12:25 PDB GW µg/L 1.9 = 0.5 U 0.7 = 0.6 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐022014 SFMW‐39‐D2‐2 2/18/2014 12:23 PDB GW µg/L 2.2 = 0.5 U 0.9 = 0.5 U 0.5 USFMW‐39 (D2) D2 F6PM6 SFMW‐39‐D2‐8 2/18/2013 9:10 PDB GW µg/L 2.8 = 0.5 U 0.69 = 2.6 = 0.5 USFMW‐39 (D2) D2 F6PM5 SFMW‐39‐D2‐2 2/18/2013 9:05 PDB GW µg/L 2.9 = 0.5 U 1.4 = 1.5 = 0.5 USFMW‐39 (D2) D2 F5G50 SFMW‐39‐D2‐8‐FD 2/28/2012 8:30 PDB GW µg/L 3.6 = 0.5 U 0.92 = 2.8 = 0.5 USFMW‐39 (D2) D2 F5G49 SFMW‐39‐D2‐8 2/28/2012 8:27 PDB GW µg/L 4.1 = 0.5 U 0.99 = 3.1 = 0.5 USFMW‐39 (D2) D2 F5G48 SFMW‐39‐D2‐2 2/28/2012 8:21 PDB GW µg/L 4.5 = 0.5 U 2 = 1.1 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q111 SFMW‐39‐D2‐8 2/14/2011 12:31 PDB GW µg/L 6 = 0.5 U 2.6 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q111 SFMW‐39‐D2‐2 2/14/2011 12:28 PDB GW µg/L 6.6 = 0.5 U 3.2 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐8_100202 SFMW‐39‐D2‐8 2/2/2010 9:18 PDB GW µg/L 6.4 = 0.5 U 3.7 = 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 60 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐39 (D2) D2 SFMW‐39‐d2‐2_100202 SFMW‐39‐D2‐2 2/2/2010 9:15 PDB GW µg/L 7 = 0.5 U 4.2 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q209 SFMW‐39‐D2‐2 4/21/2009 10:24 PDB GW µg/L 7.5 J 0.5 UJ 4.4 J 0.5 UJ 0.5 UJSFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q209 SFMW‐39‐D2‐8 4/21/2009 10:20 PDB GW µg/L 7.2 J 0.5 UJ 5.4 J 0.5 J 0.5 UJSFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q408 SFMW‐39‐D2‐8 10/6/2008 14:36 PDB GW µg/L 8.1 = 0.5 U 4.3 = 1.1 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q408 SFMW‐39‐D2‐2 10/6/2008 14:35 PDB GW µg/L 9 = 0.5 U 5.4 = 0.5 U 0.5 USFMW‐39 (D2) D2 F2RX6 SFMW‐39‐D2‐2 4/14/2008 0:00 PDB GW µg/L 9.6 = 0.5 U 4.8 = 1.7 = 0.5 USFMW‐39 (D2) D2 F2RX7 SFMW‐39‐D2‐8 4/14/2008 0:00 PDB GW µg/L 7.3 = 0.55 = 3.4 = 12 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q407 SFMW‐39‐D2‐2 10/1/2007 9:40 PDB GW µg/L 9.8 = 0.5 U 7 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q407 SFMW‐39‐D2‐8 10/1/2007 9:35 PDB GW µg/L 9 = 0.5 U 4.3 = 1.8 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐8_070219 SFMW‐39‐D2‐8 2/19/2007 10:30 PDB GW µg/L 8.5 JL 0.5 UJ 2 JL 6.9 JL 0.5 UJSFMW‐39 (D2) D2 SFMW‐39‐D2‐2_070219 SFMW‐39‐D2‐2 2/19/2007 10:24 PDB GW µg/L 8.1 JL 0.5 UJ 2 JL 7.4 JL 0.5 UJSFMW‐39 (D2) D2 F26A5 SFMW‐39‐D2‐8 8/28/2006 11:55 PDB GW µg/L 7.1 = 0.5 U 1.3 = 5.1 = 0.5 USFMW‐39 (D2) D2 F26A4 SFMW‐39‐D2‐2 8/28/2006 11:50 PDB GW µg/L 5.4 = 0.5 U 1 = 5.3 = 0.5 USFMW‐39 (D2) D2 F1YP7 SFMW‐39‐D2‐2 2/6/2006 12:35 PDB GW µg/L 7.7 = 0.5 U 1.6 = 9 = 0.5 USFMW‐39 (D2) D2 F1YP8 SFMW‐39‐D2‐8 2/6/2006 12:33 PDB GW µg/L 8 = 0.5 U 1.6 = 8.6 = 0.5 USFMW‐39 (D2) D2 F1NY9 SFMW‐39‐D2‐8 7/11/2005 8:40 PDB GW µg/L 8.9 = 0.5 U 2 = 17 = 0.5 USFMW‐39 (D2) D2 F1NY7 SFMW‐39‐D2‐5 7/11/2005 8:30 PDB GW µg/L 6.4 = 0.5 U 1.5 = 8.2 = 0.5 USFMW‐39 (D2) D2 F1NY6 SFMW‐39‐D2‐2 7/11/2005 8:20 PDB GW µg/L 6.5 = 0.5 U 1.5 = 9.2 = 0.5 USFMW‐39 (D2) D2 F1DS2 SFMW‐39‐D2‐8 4/20/2005 9:35 PDB GW µg/L 5.4 = 0.5 U 1.3 = 5.2 = 0.5 USFMW‐39 (D2) D2 F1DS0 SFMW‐39‐D2‐5 4/20/2005 9:32 PDB GW µg/L 5.4 = 0.5 U 1.4 = 6.4 = 0.5 USFMW‐39 (D2) D2 F1DR9 SFMW‐39‐D2‐2 4/20/2005 9:30 PDB GW µg/L 5.7 = 0.5 U 1.3 = 7.2 = 0.5 USFMW‐39 (D2) D2 F17Z3 SFMW‐39‐D2‐8 11/8/2004 9:35 PDB GW µg/L 7 Jv 0.5 UJv 2.1 Jv 7.2 Jv 0.5 USFMW‐39 (D2) D2 F17Z1 SFMW‐39‐D2‐5 11/8/2004 9:30 PDB GW µg/L 6.1 = 0.5 U 1.6 J 4.4 = 0.5 USFMW‐39 (D2) D2 F17Z0 SFMW‐39‐D2‐2 11/8/2004 9:25 PDB GW µg/L 9 = 0.5 U 1.5 = 5.8 = 0.29 LJSFMW‐39 (D2) D2 SFMW39‐020301 NA 3/1/2002 13:55 unknown GW µg/L 8.8 = 1 U 2 = 17 = 1 USFMW‐39 (D2) D2 FGT03 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 9 = 1 U 2 = 14 = 1 USFMW‐39 (D2) D2 FGS99 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 = 1 U 2 = 15 = 1 USFMW‐39 (D2) D2 FW542 NA 2/7/2000 0:00 unknown GW µg/L 9 = 1 U 2 = 19 = 1 U
SFMW‐40 (D3) 5/10/2020 0:00 unknownSFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐022014 SFMW‐40‐D3‐12 2/18/2014 12:41 PDB GW µg/L 4.4 = 0.5 U 0.7 = 8.5 = 0.5 USFMW‐40 (D3) D3 F6PM7 SFMW‐40‐D3‐12 2/18/2013 9:45 PDB GW µg/L 5.3 = 0.3 LJ 0.86 = 9 = 0.5 USFMW‐40 (D3) D3 F5G51 SFMW‐40‐D3‐12 2/28/2012 8:43 PDB GW µg/L 3.9 = 0.5 U 0.76 = 7.2 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐Q111 SFMW‐40‐D3‐12 2/14/2011 12:39 PDB GW µg/L 4.2 = 0.5 U 0.9 = 6.6 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12_100202‐FD SFMW‐40‐D3‐12 2/2/2010 8:55 PDB GW µg/L 4.2 = 0.5 U 1.1 = 6.3 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12_100202 SFMW‐40‐D3‐12 2/2/2010 8:55 PDB GW µg/L 4.4 = 0.5 U 1.1 = 6.6 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐Q209 SFMW‐40‐D3‐12 4/21/2009 10:30 PDB GW µg/L 4.9 J 0.5 UJ 2.1 J 5.0 J 0.5 UJSFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐Q407 SFMW‐40‐D3‐12 10/1/2007 9:00 PDB GW µg/L 4.9 = 0.5 U 1.3 = 5.1 = 0.5 USFMW‐40 (D3) D3 F1NZ3 SFMW‐40‐D3‐17 7/11/2005 9:05 PDB GW µg/L 5.7 = 0.5 U 2.2 = 4.8 = 0.14 LJSFMW‐40 (D3) D3 F1NZ2 SFMW‐40‐D3‐12 7/11/2005 9:00 PDB GW µg/L 6.2 = 0.5 U 1.8 = 4.8 = 0.16 LJSFMW‐40 (D3) D3 F1NZ1 SFMW‐40‐D3‐7 7/11/2005 8:55 PDB GW µg/L 6.8 = 0.5 U 1.9 = 4.8 = 0.16 LJ
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 61 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐40 (D3) D3 F1NZ0 SFMW‐40‐D3‐2 7/11/2005 8:50 PDB GW µg/L 5.7 = 0.5 U 2.3 = 3.9 = 0.5 USFMW‐40 (D3) D3 F1DS6 SFMW‐40‐D3‐17 4/20/2005 10:16 PDB GW µg/L 5.7 = 0.5 U 1.7 = 3.9 = 0.5 USFMW‐40 (D3) D3 F1DS5 SFMW‐40‐D3‐12 4/20/2005 10:14 PDB GW µg/L 5.8 = 0.5 U 1.5 = 3.7 = 0.5 USFMW‐40 (D3) D3 F1DS4 SFMW‐40‐D3‐7 4/20/2005 10:12 PDB GW µg/L 5.9 = 0.5 U 1.6 = 3.8 = 0.5 USFMW‐40 (D3) D3 F1DS3 SFMW‐40‐D3‐2 4/20/2005 10:09 PDB GW µg/L 5.1 = 0.5 U 1.9 = 3.6 = 0.24 LJSFMW‐40 (D3) D3 F17Z7 SFMW‐40‐D3‐17 11/8/2004 10:25 PDB GW µg/L 9.1 = 0.5 U 1.2 = 4.7 = 0.5 USFMW‐40 (D3) D3 F17Z6 SFMW‐40‐D3‐12 11/8/2004 10:20 PDB GW µg/L 8.1 = 0.5 U 1 = 4.6 = 0.5 USFMW‐40 (D3) D3 F17Z5 SFMW‐40‐D3‐7 11/8/2004 10:15 PDB GW µg/L 8.4 = 0.5 U 1.1 = 4.7 = 0.5 USFMW‐40 (D3) D3 F17Z4 SFMW‐40‐D3‐2 11/8/2004 10:10 PDB GW µg/L 8 Jv 0.5 U 1.1 Jv 4.4 = 0.5 USFMW‐40 (D3) D3 SFMW40‐020305 NA 3/5/2002 9:30 unknown GW µg/L 6 = 1 U 1.7 = 5.5 = 1 USFMW‐40 (D3) D3 FW587 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 7 = 1 U 2 = 7 = 1 USFMW‐40 (D3) D3 FW555 NA 2/8/2000 0:00 unknown GW µg/L 6 = 1 U 2 = 6 = 1 U
SFMW‐41 (D3/D4) NA 5/10/2020 0:00 unknownSFMW-41 (D3/D4) D3/D4 SFMW-41-D3/D4-5-0814 SFMW-41-D3/D4-5 8/25/2014 11:20 PDB GW ug/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐022014 SFMW‐41‐D3/D4‐5 2/18/2014 12:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐0813 SFMW‐41‐D3/D4‐5 8/12/2013 12:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 USFMW‐41 (D3/D4) D3/D4 F6PM8 SFMW‐41‐D3/D4‐5 2/18/2013 9:25 PDB GW µg/L 0.5 U 0.27 LJ 0.5 U 0.36 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F6CG8 SFMW‐41‐D3/D4‐5 8/21/2012 8:08 PDB GW µg/L 0.17 LJ 0.32 LJ 0.5 U 0.75 = 0.5 USFMW‐41 (D3/D4) D3/D4 F5G52 SFMW‐41‐D3/D4‐5 2/28/2012 8:58 PDB GW µg/L 0.5 U 0.3 LJ 0.5 U 0.31 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F4EG4 SFMW‐41‐D3/D4‐5‐Q311 8/23/2011 9:00 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.1 LJ 2.0 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐Q111 SFMW‐41‐D3/D4‐5 2/14/2011 12:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐41 (D3/D4) D3/D4 F3LQ1 SFMW‐41‐D3/D4‐5‐Q310 9/2/2010 14:00 PDB GW µg/L 0.39 LJ 0.64 = 0.5 U 1 = 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5_100202 SFMW‐41‐D3/D4‐5 2/2/2010 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 USFMW‐41 (D3/D4) D3/D4 F3B15 SFMW‐41‐D3/D4‐5 10/26/2009 13:38 PDB GW µg/L 0.72 = 1 = 0.5 U 1.6 = 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐Q209 SFMW‐41‐D3/D4‐5 4/21/2009 10:45 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3‐5‐Q407 SFMW‐41‐D3‐5 10/1/2007 9:20 PDB GW µg/L 0.5 U 0.5 = 0.5 U 1.3 = 0.5 USFMW‐41 (D3/D4) D3/D4 F1NZ6 SFMW‐41‐D4‐8 7/11/2005 9:30 PDB GW µg/L 0.5 U 0.42 LJ 0.5 U 0.32 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1NZ5 SFMW‐41‐D4‐5 7/11/2005 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.62 = 0.5 USFMW‐41 (D3/D4) D3/D4 F1NZ4 SFMW‐41‐D4‐2 7/11/2005 9:20 PDB GW µg/L 0.5 U 0.31 LJ 0.5 U 0.56 = 0.5 USFMW‐41 (D3/D4) D3/D4 F1DS9 SFMW‐41‐D4‐8 4/20/2005 11:00 PDB GW µg/L 0.5 U 0.27 LJ 0.5 U 0.33 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1DS8 SFMW‐41‐D4‐5 4/20/2005 10:57 PDB GW µg/L 0.5 U 0.4 LJ 0.5 U 0.35 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1DS7 SFMW‐41‐D4‐2 4/20/2005 10:54 PDB GW µg/L 0.5 U 0.41 LJ 0.5 U 0.44 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1801 SFMW‐41‐D4‐8 11/8/2004 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1800 SFMW‐41‐D4‐5 11/8/2004 10:50 PDB GW µg/L 0.5 U 0.23 LJ 0.5 U 0.21 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F17Z9 SFMW‐41‐D4‐2 11/8/2004 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW41‐020304 NA 3/4/2002 14:30 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐41 (D3/D4) D3/D4 FW579 NA 5/1/2000 0:00 GRN‐PUMP DUKE GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐41 (D3/D4) D3/D4 FW563 NA 2/9/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐42 unknown NA 5/10/2020 0:00 unknownSFMW‐42 unknown FW556 NA 2/8/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 62 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐42 unknown FFT54 NA 5/1/2000 0:00 BAIL GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐43 (D3) 5/10/2020 0:00 unknown
SFMW‐43 (D3) D3 F3LQ2 SFMW‐43‐D3‐Q310 9/2/2010 11:30 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.57 = 0.5 USFMW‐44 (D2) 5/10/2020 0:00 unknown
SFMW-44 (D2) D2 SFMW-44-D2-12-0814 SFMW-44-D2-12 8/25/2014 8:55 PDB GW ug/L 7.6 = 1.1 = 3.0 = 14.3 = 0.5 USFMW-44 (D2) D2 SFMW-44-D2-17-0814 SFMW-44-D2-17 8/25/2014 8:50 PDB GW ug/L 6.8 = 0.9 = 2.7 = 13.1 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐022014 SFMW‐44‐D2‐17 2/17/2014 12:53 PDB GW µg/L 5.7 = 0.5 U 2.4 = 10.4 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐022014 SFMW‐44‐D2‐12 2/17/2014 12:40 PDB GW µg/L 7.4 = 0.8 = 3 = 13.2 = 0.5 =SFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐0813 SFMW‐44‐D2‐17 8/12/2013 11:35 PDB GW µg/L 4.8 = 0.6 = 2 = 9 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐0813 SFMW‐44‐D2‐12 8/12/2013 11:30 PDB GW µg/L 5.3 = 0.6 = 2.1 = 9.8 = 0.5 USFMW‐44 (D2) D2 F6PN0 SFMW‐44‐D2‐17 2/19/2013 10:25 PDB GW µg/L 5.4 = 0.62 = 2.3 = 7.8 = 0.5 USFMW‐44 (D2) D2 F6PM9 SFMW‐44‐D2‐12 2/19/2013 10:20 PDB GW µg/L 5.7 = 0.59 = 2.6 = 8.5 = 0.5 USFMW‐44 (D2) D2 F6CH0 SFMW‐44‐D2‐17 8/21/2012 7:38 PDB GW µg/L 4.7 = 0.71 UM 1.8 = 7.6 = 0.5 USFMW‐44 (D2) D2 F6CG9 SFMW‐44‐D2‐12 8/21/2012 7:36 PDB GW µg/L 4.6 = 0.77 UM 1.7 = 8.0 = 0.5 USFMW‐44 (D2) D2 F5G54 SFMW‐44‐D2‐17 2/28/2012 12:05 PDB GW µg/L 4.5 = 0.56 = 1.9 = 9.8 = 0.5 USFMW‐44 (D2) D2 F5G53 SFMW‐44‐D2‐12 2/28/2012 11:58 PDB GW µg/L 4.1 = 0.54 = 1.7 = 9.1 = 0.5 USFMW‐44 (D2) D2 F4EG7 SFMW‐44‐D2‐17‐FD‐Q311 8/22/2011 10:58 PDB GW µg/L 6.4 = 5.0 U 2.8 LJ 13 = 2.0 USFMW‐44 (D2) D2 F4EG6 SFMW‐44‐D2‐17‐Q311 8/22/2011 10:57 PDB GW µg/L 5.4 = 5.0 U 2.1 LJ 10 = 2.0 USFMW‐44 (D2) D2 F4EG5 SFMW‐44‐D2‐12‐Q311 8/22/2011 10:56 PDB GW µg/L 5.9 = 5.0 U 2.2 LJ 11 = 2.0 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q111 SFMW‐44‐D2‐17 2/14/2011 12:00 PDB GW µg/L 5.4 = 1.5 = 1.8 = 11.2 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q111 SFMW‐44‐D2‐12 2/14/2011 11:58 PDB GW µg/L 5.6 = 1.6 = 1.9 = 11.4 = 0.5 USFMW‐44 (D2) D2 F3LQ5 SFMW‐44‐D2‐17‐Q310 8/31/2010 13:45 PDB GW µg/L 5 = 0.79 = 2 = 8.5 = 0.5 USFMW‐44 (D2) D2 F3LR1 SFMW‐44‐D2‐12‐Q310 8/31/2010 13:45 PDB GW µg/L 5.3 = 0.84 = 1.6 = 8.7 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17_100201 SFMW‐44‐D2‐17 2/1/2010 12:20 PDB GW µg/L 9.6 = 1.1 = 3.8 = 19 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12_100201 SFMW‐44‐D2‐12 2/1/2010 12:18 PDB GW µg/L 10.7 = 1.1 = 3.7 = 20.4 = 0.5 USFMW‐44 (D2) D2 F3B43 SFMW‐44‐D2‐17 10/27/2009 8:44 PDB GW µg/L 6 = 0.89 = 2.1 = 9.7 = 0.5 USFMW‐44 (D2) D2 F3B16 SFMW‐44‐D2‐12 10/26/2009 14:24 PDB GW µg/L 6.5 = 1.1 = 2.3 = 12 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q209 SFMW‐44‐D2‐17 4/20/2009 10:29 PDB GW µg/L 5.6 J 0.6 J 2.4 J 9.4 J 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q209 SFMW‐44‐D2‐12 4/20/2009 10:22 PDB GW µg/L 5.2 J 0.5 J 2.3 J 8.4 J 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q408 SFMW‐44‐D2‐17 10/6/2008 13:21 PDB GW µg/L 5.7 = 0.6 = 2.4 = 9.3 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q408 SFMW‐44‐D2‐12 10/6/2008 13:19 PDB GW µg/L 5.5 = 0.5 = 2.3 = 8.5 = 0.5 USFMW‐44 (D2) D2 F2RX8 SFMW‐44‐D2‐12 4/14/2008 0:00 PDB GW µg/L 7.3 = 0.58 = 3.2 = 12 = 0.5 USFMW‐44 (D2) D2 F2RX9 SFMW‐44‐D2‐17 4/14/2008 0:00 PDB GW µg/L 4.6 = 0.5 U 1.5 = 7.7 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q407 SFMW‐44‐D2‐17 10/1/2007 10:13 PDB GW µg/L 6.1 = 0.6 = 3.1 = 10.1 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q407 SFMW‐44‐D2‐12 10/1/2007 10:05 PDB GW µg/L 6.1 = 0.5 = 3.1 = 9.8 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12_070219 SFMW‐44‐D2‐12 2/19/2007 11:18 PDB GW µg/L 7.5 JL 1 JL 3 JL 13.9 JL 0.5 UJSFMW‐44 (D2) D2 SFMW‐44‐D2‐17_070219 SFMW‐44‐D2‐17 2/19/2007 11:13 PDB GW µg/L 7.2 JL 1.1 JL 3 JL 13.6 JL 0.5 UJSFMW‐44 (D2) D2 F26A7 SFMW‐44‐D2‐17 8/28/2006 12:34 PDB GW µg/L 3.7 = 0.5 U 1.8 = 6.6 = 0.5 USFMW‐44 (D2) D2 F26A6 SFMW‐44‐D2‐12 8/28/2006 12:27 PDB GW µg/L 3.7 = 0.5 U 1.7 = 6.6 = 0.5 USFMW‐44 (D2) D2 F1YW4 SFMW‐44‐D2‐12 2/6/2006 11:12 PDB GW µg/L 3.8 = 0.5 U 1.8 = 5.9 J 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 63 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐44 (D2) D2 F1YW5 SFMW‐44‐D2‐17 2/6/2006 11:10 PDB GW µg/L 4.7 = 0.5 U 2.3 = 7.3 = 0.5 USFMW‐44 (D2) D2 F1P69 SFMW‐44‐D2‐17 7/12/2005 9:44 PDB GW µg/L 6.7 = 1.2 = 3 = 13 = 0.5 USFMW‐44 (D2) D2 F1P68 SFMW‐44‐D2‐12 7/12/2005 9:40 PDB GW µg/L 5 = 0.84 = 2.3 = 9.7 J 0.5 USFMW‐44 (D2) D2 F1P66 SFMW‐44‐D2‐7 7/12/2005 9:35 PDB GW µg/L 6 = 1.1 = 2.7 = 11 = 0.5 USFMW‐44 (D2) D2 F1P65 SFMW‐44‐D2‐2 7/12/2005 9:32 PDB GW µg/L 6.4 = 0.68 = 3.1 = 12 = 0.5 USFMW‐44 (D2) D2 F1E17 SFMW‐44‐D2‐17 4/20/2005 11:22 PDB GW µg/L 4.6 = 0.83 = 1.8 = 7.5 = 0.5 USFMW‐44 (D2) D2 F1E16 SFMW‐44‐D2‐12 4/20/2005 11:17 PDB GW µg/L 4.8 = 0.88 = 1.7 = 7.7 = 0.5 USFMW‐44 (D2) D2 F1E14 SFMW‐44‐D2‐7 4/20/2005 11:12 PDB GW µg/L 4.5 = 1.2 = 1.6 = 7.5 = 0.5 USFMW‐44 (D2) D2 F1E13 SFMW‐44‐D2‐2 4/20/2005 11:09 PDB GW µg/L 4.1 = 0.55 = 1.8 = 6.8 = 0.5 USFMW‐44 (D2) D2 F1D97 SFMW‐44‐D2 4/19/2005 16:17 LFS GW µg/L 4.8 = 0.62 = 1.6 = 9.1 = 0.18 LJSFMW‐44 (D2) D2 F17D0 SFMW‐44‐D2 11/9/2004 14:30 LFS GW µg/L 7.2 = 1.3 = 2.2 = 12 = 0.5 USFMW‐44 (D2) D2 F1806 SFMW‐44‐D2‐17 11/9/2004 14:20 PDB GW µg/L 5.8 J 1.5 J 1.7 J 11 J 0.5 UJSFMW‐44 (D2) D2 F1805 SFMW‐44‐D2‐12 11/9/2004 14:15 PDB GW µg/L 5 J 1.4 J 1.7 J 11 J 0.5 UJSFMW‐44 (D2) D2 F1803 SFMW‐44‐D2‐7 11/9/2004 14:10 PDB GW µg/L 4.7 = 1.3 = 1.6 = 9.0 = 0.5 USFMW‐44 (D2) D2 F1802 SFMW‐44‐D2‐2 11/9/2004 14:05 PDB GW µg/L 4.4 = 1 = 1.6 = 7.8 = 0.5 USFMW‐44 (D2) D2 SFMW‐74 NA 4/22/2002 12:05 unknown GW µg/L 4.2 = 2.1 = 1.7 = 7.9 = 1 <SFMW‐44 (D2) D2 SFMW‐44 NA 4/22/2002 11:55 unknown GW µg/L 4 = 2.1 = 1.5 = 7.6 = 1 <
SFMW‐45 (D2) 5/10/2020 0:00 unknownSFMW‐45 (D2) D2 F6PN1 SFMW‐45‐D2‐2 2/18/2013 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.9 = 0.5 USFMW‐45 (D2) D2 F3S30 SFMW‐45‐D2‐2 2/15/2011 13:44 PDB GW µg/L 0.71 = 0.5 U 0.36 LJ 3.6 J 0.5 USFMW‐45 (D2) D2 SFMW‐45‐D2‐2‐Q407 SFMW‐45‐D2‐2 10/2/2007 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐45 (D2) D2 F1P86 SFMW‐45‐D2‐8 7/12/2005 12:25 PDB GW µg/L 0.28 LJ 0.5 U 0.1 LJ 0.63 = 0.5 USFMW‐45 (D2) D2 F1P85 SFMW‐45‐D2‐5 7/12/2005 12:23 PDB GW µg/L 0.4 LJ 0.5 U 0.16 LJ 1.1 = 0.5 USFMW‐45 (D2) D2 F1P83 SFMW‐45‐D2‐2 7/12/2005 12:19 PDB GW µg/L 0.48 LJ 0.5 U 0.2 LJ 2.1 = 0.5 USFMW‐45 (D2) D2 F1E34 SFMW‐45‐D2‐8 4/18/2005 14:30 PDB GW µg/L 0.15 LJ 0.5 UJv 0.5 U 0.23 LJ 0.5 USFMW‐45 (D2) D2 F1E33 SFMW‐45‐D2‐5 4/18/2005 14:25 PDB GW µg/L 0.65 = 0.5 U 0.11 LJ 0.36 LJ 0.26 LJSFMW‐45 (D2) D2 F1E31 SFMW‐45‐D2‐2 4/18/2005 14:20 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.39 LJ 0.5 USFMW‐45 (D2) D2 F17T7 SFMW‐45‐D2‐8 11/8/2004 15:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.24 LJ 0.5 USFMW‐45 (D2) D2 F17T6 SFMW‐45‐D2‐5 11/8/2004 15:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.39 LJ 0.5 USFMW‐45 (D2) D2 F17T4 SFMW‐45‐D2‐2 11/8/2004 15:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.33 LJ 0.5 USFMW‐45 (D2) D2 SFMW‐45 NA 4/22/2002 15:50 unknown GW µg/L 1 < 1 < 1 < 3.1 = 1 <
SFMW‐46 (D1/D2) 5/10/2020 0:00 unknownSFMW-46 (D1/D2) D1/D2 SFMW-46-D1/D2-2-0814 SFMW-46-D1/D2-2 8/25/2014 10:48 PDB GW ug/L 1.2 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2‐022014‐FD SFMW‐46‐D1/D2‐2 2/18/2014 13:20 PDB GW µg/L 1 = 0.5 U 0.5 U 0.8 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2‐022014 SFMW‐46‐D1/D2‐2 2/18/2014 12:20 PDB GW µg/L 0.9 = 0.5 U 0.5 U 0.6 = 0.5 USFMW‐46 (D1/D2) D1/D2 F6PN2 SFMW‐46‐D1/D2‐2 2/13/2013 11:45 PDB GW µg/L 1.2 = 0.5 U 0.22 LJ 1.2 = 0.5 USFMW‐46 (D1/D2) D1/D2 F6CH1 SFMW‐46‐D1/D2‐2 8/20/2012 11:00 PDB GW µg/L 1.2 = 0.5 U 0.32 LJ 0.93 J^ 0.5 USFMW‐46 (D1/D2) D1/D2 F5G55 SFMW‐46‐D1/D2‐2 2/28/2012 12:30 PDB GW µg/L 0.94 = 0.5 U 0.5 U 0.98 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D‐2‐Q111‐FD SFMW‐46‐D1/D2‐2 2/14/2011 14:30 PDB GW µg/L 1.3 = 0.5 U 0.7 = 1 = 1.1 =SFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2‐Q111 SFMW‐46‐D1/D2‐2 2/14/2011 13:30 PDB GW µg/L 1.1 = 0.5 U 0.5 = 0.8 = 0.6 =
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 64 OF 72
011431
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2_100201‐FD SFMW‐46‐D1/D2‐2 2/1/2010 11:43 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2_100201 SFMW‐46‐D1/D2‐2 2/1/2010 11:41 PDB GW µg/L 1.2 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1‐2‐Q408 SFMW‐46‐D1‐2 10/6/2008 13:58 PDB GW µg/L 1.9 = 0.5 U 0.6 = 1.4 = 0.5 USFMW‐46 (D1/D2) D2/D3 SFMW‐46‐D2/D3‐2‐Q407 SFMW‐46‐D2/D3‐2 10/2/2007 10:02 PDB GW µg/L 2 = 0.5 U 0.5 = 3.2 = 0.5 USFMW‐46 (D1/D2) D1/D2 F26A9 SFMW‐46‐D1/D2‐2 8/28/2006 14:35 PDB GW µg/L 0.93 = 0.5 U 0.5 U 2.6 = 0.5 USFMW‐46 (D1/D2) D1/D2 F1P91 SFMW‐46‐D1/D2‐17 7/12/2005 13:13 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 2.7 = 0.13 LJSFMW‐46 (D1/D2) D1/D2 F1P87 SFMW‐46‐D1/D2‐2 7/12/2005 13:12 PDB GW µg/L 1.4 = 0.5 U 0.27 LJ 4.7 = 0.065 LJSFMW‐46 (D1/D2) D1/D2 F1P90 SFMW‐46‐D1/D2‐12 7/12/2005 13:11 PDB GW µg/L 2.1 = 0.5 U 0.4 LJ 2.9 = 0.14 LJSFMW‐46 (D1/D2) D1/D2 F1P88 SFMW‐46‐D1/D2‐7 7/12/2005 13:11 PDB GW µg/L 2.1 = 0.5 U 0.4 LJ 2.8 = 0.14 LJSFMW‐46 (D1/D2) D1/D2 F1E39 SFMW‐46‐D1/D2‐17 4/18/2005 9:15 PDB GW µg/L 1.7 = 0.5 U 0.32 LJ 3.0 = 0.14 LJSFMW‐46 (D1/D2) D1/D2 F1E38 SFMW‐46‐D1/D2‐12 4/18/2005 9:10 PDB GW µg/L 1.8 = 0.5 U 0.36 LJ 2.9 = 0.5 USFMW‐46 (D1/D2) D1/D2 F1E36 SFMW‐46‐D1/D2‐7 4/18/2005 9:00 PDB GW µg/L 2.1 = 0.5 U 0.39 LJ 3.0 = 0.18 LJSFMW‐46 (D1/D2) D1/D2 F1E35 SFMW‐46‐D1/D2‐2 4/18/2005 8:45 PDB GW µg/L 1.5 = 0.5 U 0.29 LJ 6.0 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17W1 SFMW‐46‐D1/D2‐17 11/9/2004 14:55 PDB GW µg/L 1.8 = 0.5 U 0.33 LJ 2.4 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17W0 SFMW‐46‐D1/D2‐12 11/9/2004 14:50 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 2.8 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17T9 SFMW‐46‐D1/D2‐7 11/9/2004 14:45 PDB GW µg/L 2.2 = 0.5 U 0.39 LJ 2.9 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17T8 SFMW‐46‐D1/D2‐2 11/9/2004 14:40 PDB GW µg/L 2.1 = 0.5 U 0.35 LJ 3.9 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46 NA 4/22/2002 17:40 unknown GW µg/L 1.4 = 1 < 1 < 4.9 = 1 <SFMW‐46 (D2) D1/D2 SFMW‐46‐D1/D2‐2‐0813 SFMW‐46‐D1/D2‐2 8/13/2013 8:45 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.2 = 0.5 U
SFMW‐47 (I1/I2) NA 5/10/2020 0:00 unknownSFMW-47 (I1/I2) I1/I2 SFMW-47-I1/I2-22-0814 SFMW-47-I1/I2-22 8/25/2014 8:46 PDB GW ug/L 6.2 = 0.5 U 0.9 = 25.2 = 0.5 USFMW-47 (I1/I2) I1/I2 SFMW-47-I1/I2-12-0814 SFMW-47-I1/I2-12 8/25/2014 8:44 PDB GW ug/L 5.8 = 0.5 U 1.0 = 22.6 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐022014 SFMW‐47‐I1/I2‐22 2/18/2014 8:40 PDB GW µg/L 5.3 = 0.5 U 0.7 = 20.6 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐022014 SFMW‐47‐I1/I2‐12 2/18/2014 8:37 PDB GW µg/L 4.9 = 0.5 U 0.6 = 18.5 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐0813FD SFMW‐47‐I1/I2‐12FD 8/12/2013 11:50 PDB GW µg/L 4.8 = 0.5 U 0.6 = 17.8 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐0813 SFMW‐47‐I1/I2‐22 8/12/2013 10:53 PDB GW µg/L 5.2 = 0.5 U 0.6 = 20.9 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐0813 SFMW‐47‐I1/I2‐12 8/12/2013 10:50 PDB GW µg/L 5 = 0.5 U 0.6 = 19.1 = 0.5 USFMW‐47 (I1/I2) I1/I2 F6PN4 SFMW‐47‐I1/I2‐22 2/12/2013 11:15 PDB GW µg/L 6.4 = 0.52 = 1.1 = 19 = 0.64 =SFMW‐47 (I1/I2) I1/I2 F6PN3 SFMW‐47‐I1/I2‐12 2/12/2013 11:10 PDB GW µg/L 5.4 = 0.5 U 0.67 = 18 = 0.5 USFMW‐47 (I1/I2) I1/I2 F6CD2 SFMW‐47‐I1/I2‐12 8/21/2012 9:46 PDB GW µg/L 4.5 = 0.5 U 0.52 = 15 = 0.5 USFMW‐47 (I1/I2) I1/I2 F6CG5 SFMW‐47‐I1/I2‐22‐FD 8/21/2012 8:44 PDB GW µg/L 4.5 = 0.5 U 0.55 = 15 = 0.5 USFMW‐47 (I1/I2) I1/I2 F6CB9 SFMW‐47‐I1/I2‐22 8/20/2012 14:06 PDB GW µg/L 4.0 = 0.13 LJ 0.61 LJ 14 = 1.0 USFMW‐47 (I1/I2) I1/I2 F5GB4 SFMW‐47‐I1/I2‐12‐FD 2/27/2012 13:15 PDB GW µg/L 3.3 = 0.5 U 0.47 LJ 13 = 0.5 USFMW‐47 (I1/I2) I1/I2 F5GB3 SFMW‐47‐I1/I2‐12 2/27/2012 12:15 PDB GW µg/L 3.4 = 0.5 U 0.52 = 15 = 0.5 USFMW‐47 (I1/I2) I1/I2 F4EG9 SFMW‐47‐I1/I2‐22‐Q311 8/22/2011 8:00 PDB GW µg/L 3.8 LJ 5.0 U 5.0 U 14 = 2.0 USFMW‐47 (I1/I2) I1/I2 F4EG8 SFMW‐47‐I1/I2‐12‐Q311 8/22/2011 8:00 PDB GW µg/L 5.6 = 5.0 U 5.0 U 20 = 2.0 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐Q11 SFMW‐47‐I1/I2‐22 2/14/2011 8:34 PDB GW µg/L 4.2 = 0.5 U 0.7 = 18.4 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐Q11 SFMW‐47‐I1/I2‐12 2/14/2011 8:25 PDB GW µg/L 4 = 0.5 U 0.6 = 16 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐Q310 SFMW‐47‐I1/I2‐22‐Q310 9/8/2010 8:55 PDB GW µg/L 4.6 = 0.5 U 0.6 = 18.4 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐Q310 SFMW‐47‐I1/I2‐12‐Q310 9/8/2010 8:50 PDB GW µg/L 4.3 = 0.5 U 0.6 = 16.8 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 65 OF 72
011432
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12_100201 SFMW‐47‐I1/I2‐12 2/1/2010 12:59 PDB GW µg/L 4.3 = 0.5 U 0.7 = 17 = 0.5 USFMW‐47 (I1/I2) I1/I2 F3B77 SFMW‐47‐I1/I2‐12 10/26/2009 9:37 PDB GW µg/L 3.7 = 0.5 U 0.57 = 16 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1I2‐22‐Q209 SFMW‐47‐I1/I2‐22 4/20/2009 8:36 PDB GW µg/L 5.0 J 0.5 U 0.8 J 23.4 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1‐12‐FD‐Q209 SFMW‐47‐I1/I2‐12‐FD 4/20/2009 8:31 PDB GW µg/L 4.7 J 0.5 U 0.8 J 19.3 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1I2‐12‐Q209 SFMW‐47‐I1/I2‐12 4/20/2009 8:30 PDB GW µg/L 4.9 J 0.5 U 0.8 J 22.2 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐22‐Q408 SFMW‐47‐I1/I2‐22 10/6/2008 10:50 PDB GW µg/L 5.6 = 0.5 U 0.9 = 25.8 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐12‐Q408 SFMW‐47‐I1/I2‐12 10/6/2008 10:48 PDB GW µg/L 5 = 0.5 U 0.8 = 22.3 = 0.5 USFMW‐47 (I1/I2) I1/I2 F2RY0 SFMW‐47‐I1/I2‐12 4/14/2008 0:00 PDB GW µg/L 6.5 = 0.5 U 1 = 33 = 0.5 USFMW‐47 (I1/I2) I1/I2 F2RY1 SFMW‐47‐I1/I2‐22 4/14/2008 0:00 PDB GW µg/L 6.8 = 0.5 U 1.1 = 33 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐12‐Q407 SFMW‐47‐I2‐12 10/1/2007 8:31 PDB GW µg/L 5.8 = 0.5 U 1.1 = 26.2 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐22‐Q407 SFMW‐47‐I2‐22 10/1/2007 8:29 PDB GW µg/L 6 = 0.5 U 1 = 28.2 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐12_070219 SFMW‐47‐I2‐12 2/19/2007 8:13 PDB GW µg/L 6.2 JL 0.5 UJ 1.1 JL 35.4 JL 0.5 UJSFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐22_070219 SFMW‐47‐I2‐22 2/19/2007 8:13 PDB GW µg/L 6.5 JL 0.5 UJ 1.1 JL 37 JL 0.5 UJSFMW‐47 (I1/I2) I1/I2 F26B1DL SFMW‐47‐I2‐22 8/29/2006 7:55 PDB GW µg/L 21 =SFMW‐47 (I1/I2) I1/I2 F26B1 SFMW‐47‐I2‐22 8/29/2006 7:55 PDB GW µg/L 3.9 = 0.5 U 0.58 = 0.5 USFMW‐47 (I1/I2) I1/I2 F26B0DL SFMW‐47‐I2‐12 8/29/2006 7:50 PDB GW µg/L 2.7 = 19 =SFMW‐47 (I1/I2) I1/I2 F26B0 SFMW‐47‐I2‐12 8/29/2006 7:50 PDB GW µg/L 0.5 U 0.65 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1YR3DL SFMW‐47‐I2‐22 2/6/2006 8:29 PDB GW µg/L 27 =SFMW‐47 (I1/I2) I1/I2 F1YR3 SFMW‐47‐I2‐22 2/6/2006 8:29 PDB GW µg/L 5.9 = 0.5 U 1 = 0.5 USFMW‐47 (I1/I2) I1/I2 F1YR2DL SFMW‐47‐I2‐12 2/6/2006 8:27 PDB GW µg/L 28 =SFMW‐47 (I1/I2) I1/I2 F1YR2 SFMW‐47‐I2‐12 2/6/2006 8:27 PDB GW µg/L 5.6 = 0.5 U 1 = 0.5 USFMW‐47 (I1/I2) I1/I2 F1NX8DL SFMW‐47‐I2‐27 7/13/2005 8:53 PDB GW µg/L 29 =SFMW‐47 (I1/I2) I1/I2 F1NX8 SFMW‐47‐I2‐27 7/13/2005 8:53 PDB GW µg/L 6.2 = 0.5 U 1.1 = 0.18 LJSFMW‐47 (I1/I2) I1/I2 F1NX7DL SFMW‐47‐I2‐22 7/13/2005 8:51 PDB GW µg/L 30 =SFMW‐47 (I1/I2) I1/I2 F1NX7 SFMW‐47‐I2‐22 7/13/2005 8:51 PDB GW µg/L 6.5 = 0.5 U 1.2 = 0.18 LJSFMW‐47 (I1/I2) I1/I2 F1NX6DL SFMW‐47‐I2‐17 7/13/2005 8:50 PDB GW µg/L 29 =SFMW‐47 (I1/I2) I1/I2 F1NX6 SFMW‐47‐I2‐17 7/13/2005 8:50 PDB GW µg/L 6.3 = 0.5 U 1.2 = 0.16 LJSFMW‐47 (I1/I2) I1/I2 F1NX3DL SFMW‐47‐I2‐2 7/13/2005 8:49 PDB GW µg/L 27 =SFMW‐47 (I1/I2) I1/I2 F1NX5DL SFMW‐47‐I2‐12 7/13/2005 8:49 PDB GW µg/L 28 =SFMW‐47 (I1/I2) I1/I2 F1NX3 SFMW‐47‐I2‐2 7/13/2005 8:49 PDB GW µg/L 6.3 = 0.5 U 1.2 = 0.16 LJSFMW‐47 (I1/I2) I1/I2 F1NX5 SFMW‐47‐I2‐12 7/13/2005 8:49 PDB GW µg/L 6.5 = 0.5 U 1.3 = 0.5 USFMW‐47 (I1/I2) I1/I2 F1NX4DL SFMW‐47‐I2‐7 7/13/2005 8:47 PDB GW µg/L 27 =SFMW‐47 (I1/I2) I1/I2 F1NX4 SFMW‐47‐I2‐7 7/13/2005 8:47 PDB GW µg/L 6.2 = 0.5 U 1.2 = 0.17 LJSFMW‐47 (I1/I2) I1/I2 F1DR1 SFMW‐47‐I2‐27 4/19/2005 9:54 PDB GW µg/L 9.6 = 0.5 U 1.7 = 63 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1DR0 SFMW‐47‐I2‐22 4/19/2005 9:52 PDB GW µg/L 10 = 0.5 U 1.9 = 65 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1DQ9 SFMW‐47‐I2‐17 4/19/2005 9:50 PDB GW µg/L 10 = 0.5 U 1.8 = 65 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1DQ8 SFMW‐47‐I2‐12 4/19/2005 9:48 PDB GW µg/L 7.6 = 0.5 U 1.5 = 51 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1DQ7DL SFMW‐47‐I2‐7 4/19/2005 9:46 PDB GW µg/L 48 =SFMW‐47 (I1/I2) I1/I2 F1DQ7 SFMW‐47‐I2‐7 4/19/2005 9:46 PDB GW µg/L 7.5 = 0.5 U 1.5 = 0.19 LJSFMW‐47 (I1/I2) I1/I2 F1DQ6 SFMW‐47‐I2‐2 4/19/2005 9:44 PDB GW µg/L 7.4 = 0.5 U 1.5 = 48 J 0.21 LJ
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 66 OF 72
011433
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SFMW‐47 (I1/I2) I1/I2 F17M6 SFMW‐47‐I2‐27 11/9/2004 13:20 PDB GW µg/L 6.9 = 0.5 U 1.2 = 50 J 0.5 USFMW‐47 (I1/I2) I1/I2 F17M5 SFMW‐47‐I2‐22 11/9/2004 13:17 PDB GW µg/L 6.7 = 0.5 U 1.2 = 49 J 0.37 LJSFMW‐47 (I1/I2) I1/I2 F17M4 SFMW‐47‐I2‐17 11/9/2004 13:15 PDB GW µg/L 7.4 = 0.5 U 1.3 U 55 J 0.5 USFMW‐47 (I1/I2) I1/I2 F17M3 SFMW‐47‐I2‐12 11/9/2004 13:11 PDB GW µg/L 7.8 = 0.5 U 1.3 = 56 J 0.5 USFMW‐47 (I1/I2) I1/I2 F17M2 SFMW‐47‐I2‐7 11/9/2004 13:07 PDB GW µg/L 7.8 = 0.5 U 1.3 = 49 J 0.25 LJSFMW‐47 (I1/I2) I1/I2 F17M1 SFMW‐47‐I2‐2 11/9/2004 13:06 PDB GW µg/L 7 = 0.5 U 1.3 = 45 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47 NA 4/25/2002 0:00 unknown GW µg/L 8.4 = 1 < 1.7 = 48 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47AT‐5 NA 4/16/2002 10:30 unknown GW µg/L 11.3 = 1 < 3 = 50.9 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47‐AT‐4 NA 4/15/2002 9:10 unknown GW µg/L 10.9 = 1 < 2.6 = 55.7 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47‐AT‐3 NA 4/14/2002 13:15 unknown GW µg/L 10.5 = 1 < 2.8 = 66.3 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47AT‐2 NA 4/13/2002 13:45 unknown GW µg/L 9.8 = 1 < 2.2 = 54.3 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47AT‐1 NA 4/13/2002 10:40 unknown GW µg/L 9.6 = 1 < 2.3 = 53.5 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW47 B dev‐020311 NA 3/11/2002 17:45 unknown GW µg/L 8.7 = 1 U 2 = 58 = 1 USFMW‐47 (I1/I2) I1/I2 SFMW47 P dev‐020311 NA 3/11/2002 17:15 unknown GW µg/L 5.1 = 1 U 1 = 33 = 1 U
SHB‐4/WellNo. 1 (S) NA 5/10/2020 0:00 unknownSHB‐4/WellNo. 1 (S) S FW881 NA 12/10/1996 0:00 unknown GW µg/L 0.6 J 1 U 0.6 J 1 U NDSHB‐4/WellNo. 1 (S) S 309302‐6 NA 8/31/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 5 ND 10 NDSHB‐4/WellNo. 1 (S) S 930901‐7 NA 8/31/1993 0:00 unknown GW µg/L 0.8 = <0.2 0.6 = 0.5 = NDSHB‐4/WellNo. 1 (S) S FX016 NA 8/31/1993 0:00 unknown GW µg/L 0.8 J 1 U 1 = 0.7 J NDSHB‐4/WellNo. 1 (S) S FQ928 NA 5/20/1993 0:00 unknown GW µg/L 2 J 10 U 10 U ND
SP‐5 5/10/2020 0:00 unknownSP‐5 NA FAP SP‐5 FAP‐SP‐5 6/16/2014 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP‐SP‐5 3/18/2014 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP‐SP‐5 2/17/2014 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP‐SP‐5 1/20/2014 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP‐SP‐5 12/16/2013 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP‐SP‐5 11/19/2013 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP‐SP‐5 10/28/2013 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP‐SP‐5 9/25/2013 0:00 Grab GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐18032013 FAP_SP‐5‐18032013 3/18/2013 14:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐27022012 FAP_SP‐5‐20022013 2/20/2013 14:55 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5AJ6 FAP_SP‐5‐21012013 1/21/2013 9:15 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 12/19/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 11/19/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 10/18/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 9/18/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐06082012 FAP_SP‐5‐06082012 8/6/2012 14:35 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐07162012 FAP_SP‐5‐07162012 7/16/2012 10:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5Y07 SP‐5‐19062012 6/19/2012 9:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5W96 SP‐5‐22052012 5/22/2012 14:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5LL8 FAP_SP‐5‐04162012 4/16/2012 13:01 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5HF2 FAP_SP‐5‐19032012 3/19/2012 14:17 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐27022012 FAP_SP‐5‐27022012 2/28/2012 15:20 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5AJ6 FAP_SP‐5‐16012012 1/16/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 67 OF 72
011434
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SP‐5 NA FAP SP‐5 FAP_SP‐5 12/19/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 11/22/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 10/17/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 10/17/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 9/19/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA F4EH2 SP‐5‐Q311 8/22/2011 15:20 GRAB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USP‐5 NA FAP SP‐5 FAP_SP‐5 7/18/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 6/20/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 5/24/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 4/18/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐24032011 FAP_SP‐5 3/24/2011 9:40 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5_Q111 FAP_SP‐5 2/14/2011 14:20 GRAB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSP‐5 NA FAP_SP‐5_110125 FAP_SP‐5 1/25/2011 13:40 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F3RM4 FAP_SP‐5 12/14/2010 9:55 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP‐SP‐5 FAP‐SP‐5 9/23/2010 13:46 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐Q310 SP_SP‐5‐Q310 9/7/2010 15:04 GRAB GW µg/L 2.1 = 0.5 U 0.6 = 5.0 = 0.5 USP‐5 NA FAP SP‐5‐Q409 b FAP_SP‐5 10/28/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5‐Q309 b FAP_SP‐5 7/6/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 20090603 b FAP_SP‐5 6/3/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5‐Q209 bc FAP_SP‐5 4/20/2009 0:00 GRAB GW µg/L 2.9 = 0.5 U 0.8 = 7.3 = 0.5 USP‐5 NA FAP SP‐5 090212 b FAP_SP‐5 2/12/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 081111 b FAP_SP‐5 11/11/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080707 b FAP_SP‐5 7/7/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080707‐DUP b FAP_SP‐5 7/7/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080414 b FAP_SP‐5 4/14/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080414‐DUP b FAP_SP‐5 4/14/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080218 b FAP_SP‐5 2/18/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 071029 b FAP_SP‐5 10/28/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 070823‐DUP FAP_SP‐5 8/23/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 070823 b FAP_SP‐5 8/23/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 070602 b FAP_SP‐5 6/2/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 B07 b FAP_SP‐5 2/20/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 C07 b FAP_SP‐5 2/20/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 A07 b FAP_SP‐5 2/19/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 061016 FAP_SP‐5 10/16/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 0600816 FAP_SP‐5 8/16/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 0600719 FAP_SP‐5 7/19/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 060524 FAP_SP‐5 5/24/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 060329c FAP_SP‐5 3/29/2006 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP SP‐5 060308c FAP_SP‐5 3/8/2006 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP SP‐5 060127c FAP_SP‐5 1/27/2006 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP SP‐5 051130c FAP_SP‐5 11/30/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP Treated 102505c FAP_SP‐5 10/25/2005 0:00 GRAB GW µg/L 0.8 J 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP Treated 102105c FAP_SP‐5 10/21/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP Treated 101905c FAP_SP‐5 10/19/2005 0:00 GRAB GW µg/L 0.7 J 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA EFFL. BAG FILTER DISCHARGE Cb FAP_SP‐5 3/17/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA ASTP EFFLUENTb FAP_SP‐5 2/22/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 68 OF 72
011435
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SP‐5 NA Q105ASTPEFFLUENT1b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT2b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT3b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT4b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT5b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 U
SPSC/Ice Plant NA 5/10/2020 0:00 unknownSPSC/Ice Plant unknown OR‐93‐2055 NA 8/26/1993 0:00 unknown GW µg/L 1 U 0.85 J 1 U 1 U NDSPSC/Ice Plant unknown OR‐93‐1776 NA 7/28/1993 0:00 unknown GW µg/L 2.5 = 1 = 1 U 3.6 = NDSPSC/Ice Plant unknown notassigned‐7 NA 4/26/1989 0:00 unknown GW µg/L ND ND ND NDSPSC/Ice Plant unknown notassigned‐6 NA 8/20/1987 0:00 unknown GW µg/L ND ND ND NDSPSC/Ice Plant unknown notassigned‐5 NA 12/3/1986 0:00 unknown GW µg/L ND ND ND ND
SPSC‐MW1 unknown NA 5/10/2020 0:00 unknownSPSC‐MW1 unknown 309302‐1 NA 8/31/1993 0:00 unknown GW µg/L 3 J 5 ND 3 J 3 J 10 NDSPSC‐MW1 unknown 930901‐3 NA 8/31/1993 0:00 unknown GW µg/L 3.3 = <0.2 3 = 2.8 = NDSPSC‐MW1 unknown 91158604 NA 11/7/1989 0:00 unknown GW µg/L 5.4 = <0.2 3.3 = ND
SPSC‐MW2 unknown NA 5/10/2020 0:00 unknownSPSC‐MW2 unknown 930901‐2 NA 8/31/1993 0:00 unknown GW µg/L 3 = 1.4 = 2.6 = 2.6 = NDSPSC‐MW2 unknown 309302‐7 NA 8/31/1993 0:00 unknown GW µg/L 5 ND 1 J 5 ND 5 ND NDSPSC‐MW2 unknown 930902‐16 NA 8/30/1993 0:00 unknown GW µg/L 3.6 = 0.6 = 1.7 = 4.9 = <0.2SPSC‐MW2 unknown 00153701 NA 1/3/1990 0:00 unknown GW µg/L 15 = 0.7 = 11 = ND
SPSC‐MW3 unknown NA 5/10/2020 0:00 unknownSPSC‐MW3 unknown FGF79 NA 7/30/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USPSC‐MW3 unknown FQ857 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USPSC‐MW3 unknown FW882 NA 12/10/1996 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U NDSPSC‐MW3 unknown 309302‐2 NA 8/31/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 3 J 10 NDSPSC‐MW3 unknown 930901‐1 NA 8/31/1993 0:00 unknown GW µg/L 2.5 = 1.1 = 2.4 = 3.9 = NDSPSC‐MW3 unknown 930902‐1 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐MW3 unknown 930902‐15 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐MW3 unknown 309302‐10 NA 8/30/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 5 ND NDSPSC‐MW3 unknown 00153702 NA 1/3/1990 0:00 unknown GW µg/L 1.4 = <0.2 1.1 = ND
SPSC‐MW4 unknown NA 5/10/2020 0:00 unknownSPSC‐MW4 unknown FFT53 NA 5/1/2000 0:00 BAIL GW µg/L 2 = 1 U 0.8 LJ 3 = 1 USPSC‐MW4 unknown FW554 NA 2/8/2000 0:00 unknown GW µg/L 1 = 1 U 0.7 LJ 3 = 1 USPSC‐MW4 unknown FGR70 NA 11/2/1999 0:00 unknown GW µg/L 2 = 1 U 1 = 2 = 1 USPSC‐MW4 unknown FGF61 NA 7/28/1999 0:00 unknown GW µg/L 1 = 1 U 0.6 LJ 3 = 1 USPSC‐MW4 unknown FQ809 NA 11/5/1997 0:00 unknown GW µg/L 1 = 1 U 0.7 J 3 = 1 USPSC‐MW4 unknown FW883 NA 12/10/1996 0:00 unknown GW µg/L 2 = 0 U 1 = 3 = NDSPSC‐MW4 unknown 931025‐2 NA 10/13/1993 0:00 unknown GW µg/L 1.1 = <0.2 0.6 = 1.7 = <0.2SPSC‐MW4 unknown 309302‐4 NA 8/31/1993 0:00 unknown GW µg/L 2 J 5 ND 5 ND 1 J 10 NDSPSC‐MW4 unknown 930901‐6 NA 8/31/1993 0:00 unknown GW µg/L 2.8 = 0.4 = <0.2 1.7 = NDSPSC‐MW4 unknown 930901‐4 NA 8/31/1993 0:00 unknown GW µg/L 6.2 = <0.2 2.4 = 24 = ND
SPSC‐MW5 unknown NA 5/10/2020 0:00 unknownSPSC‐MW5 unknown FQ810 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USPSC‐MW5 unknown 309302‐3 NA 8/31/1993 0:00 unknown GW µg/L 2 J 5 ND 5 ND 5 = 10 NDSPSC‐MW5 unknown 930901‐5 NA 8/31/1993 0:00 unknown GW µg/L 3.3 = <0.2 2.1 = 4.9 = NDSPSC‐MW5 unknown 930902‐3 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐MW6 unknown NA 5/10/2020 0:00 unknown
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 69 OF 72
011436
TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
SPSC‐MW6 unknown 930901‐10 NA 9/1/1993 0:00 unknown GW µg/L 7 = <0.2 2.5 = 26 = NDSPSC‐MW6 unknown 309302‐5 NA 8/31/1993 0:00 unknown GW µg/L 6 = 5 ND 5 ND 24 = 10 NDSPSC‐MW6 unknown 930902‐5 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐MW7 unknown NA 5/10/2020 0:00 unknownSPSC‐MW7 unknown 930901‐8 NA 8/31/1993 0:00 unknown GW µg/L 1.9 = 0.7 = 1.5 = <0.2 NDSPSC‐MW7 unknown 309302‐9 NA 8/31/1993 0:00 unknown GW µg/L <5 <5 <5 <5 NDSPSC‐MW7 unknown 930902‐2 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐MW7 unknown 930902‐8 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐MW8 unknown NA 5/10/2020 0:00 unknownSPSC‐MW8 unknown 930902‐9 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2SPSC‐MW8 unknown 930902‐6 NA 8/30/1993 0:00 unknown GW µg/L 0.2 = <0.2 <0.2 <0.2 <0.2
SPSC‐MWD unknown NA 5/10/2020 0:00 unknownSPSC‐MWD unknown 930902‐7 NA 8/30/1993 0:00 unknown GW µg/L 0.3 = <0.2 <0.2 0.3 = <0.2
SPSC‐W13 unknown NA 5/10/2020 0:00 unknownSPSC‐W13 unknown 930902‐11 NA 8/31/1993 0:00 unknown GW µg/L 0.3 = <0.2 <0.2 0.2 = <0.2
SPSC‐W14 unknown NA 5/10/2020 0:00 unknownSPSC‐W14 unknown 930902‐12 NA 8/31/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐W15 unknown NA 5/10/2020 0:00 unknownSPSC‐W15 unknown 930902‐4 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐W18 unknown NA 5/10/2020 0:00 unknownSPSC‐W18 unknown 930902‐10 NA 8/30/1993 0:00 unknown GW µg/L 2 = 0.3 = 0.7 = 2.3 = <0.2
SPSC‐W19 unknown NA 5/10/2020 0:00 unknownSPSC‐W19 unknown 612323‐02 NA 12/11/1996 0:00 unknown GW µg/L <1 <1 <1 <1 NDSPSC‐W19 unknown 930902‐14 NA 8/30/1993 0:00 unknown GW µg/L 0.6 = <0.2 <0.2 0.7 = <0.2SPSC‐W19 unknown 309302‐11 NA 8/30/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 5 ND ND
SPSC‐W20 unknown NA 5/10/2020 0:00 unknownSPSC‐W20 unknown 930902‐13 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
St. Jos. Supply unknown NA 5/10/2020 0:00 unknownSt. Jos. Supply unknown FGT01 NA 5/4/2000 0:00 OTHER GW µg/L 2 = 1 U 1 U 6 = 1 USt. Jos. Supply unknown FR847 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 3 = 1 USt. Jos. Supply unknown FR848 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 3 = 1 USt. Jos. Supply unknown FR849 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 3 = 1 USt. Jos. Supply unknown FR850 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 4 = 1 USt. Jos. Supply unknown FR839 NA 5/12/1998 0:00 unknown GW µg/L 2 = 1 U 1 U 10 = 1 USt. Jos. Supply unknown FR842 NA 5/12/1998 0:00 unknown GW µg/L 2 = 1 U 1 U 10 = 1 USt. Jos. Supply unknown FR840 NA 5/12/1998 0:00 unknown GW µg/L 3 = 1 U 1 U 10 = 1 USt. Jos. Supply unknown OR‐93‐3175 NA 12/8/1993 0:00 unknown GW µg/L 1 U 1.6 = 1 U 1 = NDSt. Jos. Supply unknown OR‐93‐2954 NA 11/17/1993 0:00 unknown GW µg/L 1 U 1.5 = 1 U 0.9 J NDSt. Jos. Supply unknown notassigned‐8 NA 12/3/1986 0:00 unknown GW µg/L ND ND ND ND
WB‐01 (I1/I2) NA 5/10/2020 0:00 unknownWB‐01 (I1/I2) I1/I2 F6PN5 WB‐01‐I1/I2‐27 2/18/2013 0:00 PDB GW µg/L 0.96 = 0.5 U 0.11 LJ 1.7 = 0.5 UWB‐01 (I1/I2) I1/I2 F6PN6 WB‐01‐I1/I2‐27‐FD 2/18/2013 0:00 PDB GW µg/L 1 = 0.5 U 0.5 U 2 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G60 WB‐01‐I1/I2‐27 2/27/2012 11:55 PDB GW µg/L 0.74 = 0.5 U 0.5 U 1.2 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G59 WB‐01‐I1/I2‐22 2/27/2012 11:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G57 WB‐01‐I1/I2‐17 2/27/2012 11:50 PDB GW µg/L 0.53 = 0.5 U 0.5 U 0.8 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G56 WB‐01‐I1/I2‐12 2/27/2012 11:48 PDB GW µg/L 0.49 LJ 0.5 U 0.5 U 0.78 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G61 WB‐01‐I1/I2‐7 2/27/2012 11:45 PDB GW µg/L 0.41 LJ 0.5 U 0.5 U 0.74 = 0.5 U
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 70 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
WB‐01 (I1/I2) I1/I2 F5G58 WB‐01‐I1/I2‐2 2/27/2012 11:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.58 = 0.5 UWB‐01 (I1/I2) I1/I2 F4EI1 WB‐01‐I1/I2‐27‐Q311 8/22/2011 8:02 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.8 LJ 2.0 UWB‐01 (I1/I2) I1/I2 F4EI0 WB‐01‐I1/I2‐22‐Q311 8/22/2011 8:01 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.6 LJ 2.0 UWB‐01 (I1/I2) I1/I2 F4EH8 WB‐01‐I1/I2‐17‐Q311 8/22/2011 8:00 PDB GW µg/L 1.1 LJ 5.0 U 5.0 U 1.6 LJ 2.0 UWB‐01 (I1/I2) I1/I2 F4EH7 WB‐01‐I1/I2‐12‐Q311 8/22/2011 7:55 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F4EI3 WB‐01‐I1/I2‐7‐FD‐Q311 8/22/2011 7:52 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F4EI2 WB‐01‐I1/I2‐7‐Q311 8/22/2011 7:51 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F4EH9 WB‐01‐I1/I2‐2‐Q311 8/22/2011 7:50 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F3S54 WB‐01‐I1/I2‐27 2/18/2011 8:55 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.47 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S55 WB‐01‐I1/I2‐22 2/18/2011 8:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.27 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S53 WB‐01‐I1/I2‐22 2/18/2011 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S52 WB‐01‐I1/I2‐17 2/18/2011 8:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S51 WB‐01‐I1/I2‐12 2/18/2011 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.29 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S50 WB‐01‐I1/I2‐7 2/18/2011 8:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UWB‐01 (I1/I2) I1/I2 F3S49 WB‐01‐I1/I2‐2 2/18/2011 8:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UWB‐01 (I1/I2) I FX090 NA 5/3/2000 0:00 GRN‐PUMP NMED GW µg/L 4 = 1 U 0.8 LJ 4 = 1 UWB‐01 (I1/I2) I FGF39 NA 7/27/1999 0:00 unknown GW µg/L 4 = 1 U 0.8 LJ 4 = 1 UWB‐01 (I1/I2) I FQ845 NA 11/3/1997 0:00 unknown GW µg/L 4 = 1 U 0.9 J 5 = 1 UWB‐01 (I1/I2) I 9705043‐2 NA 5/19/1997 0:00 unknown GW µg/L 2.8 = 1 ND 1 ND 3.6 = ND
WB‐01 (S) NA 5/10/2020 0:00 unknownWB‐01 (S) S FX088 NA 5/2/2000 0:00 BAIL GW µg/L 0.6 LJ 1 U 1 U 0.5 LJ 1 UWB‐01 (S) S FQ843 NA 11/3/1997 0:00 unknown GW µg/L 0.6 J 1 U 1 U 0.6 J 1 UWB‐01 (S) S 9705043‐1 NA 5/19/1997 0:00 unknown GW µg/L 1 ND 1 ND 1 ND 1 ND ND
WB‐02 (I1/I2) NA 5/10/2020 0:00 unknownWB‐02 (I1/I2) I1/I2 F6PN7 WB‐02‐I1/I2‐27 2/18/2013 12:35 PDB GW µg/L 0.57 = 0.5 U 0.5 U 0.81 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G66 WB‐02‐I1/I2‐27 2/27/2012 11:15 PDB GW µg/L 0.51 = 0.5 U 0.5 U 0.77 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G65 WB‐02‐I1/I2‐22 2/27/2012 11:12 PDB GW µg/L 0.46 LJ 0.5 U 0.5 U 0.71 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G63 WB‐02‐I1/I2‐17 2/27/2012 11:09 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 0.76 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G62 WB‐02‐I1/I2‐12 2/27/2012 11:06 PDB GW µg/L 0.5 LJ 0.5 U 0.5 U 0.73 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G68 WB‐02‐I1/I2‐7‐FD 2/27/2012 11:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.77 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G67 WB‐02‐I1/I2‐7 2/27/2012 11:02 PDB GW µg/L 0.59 = 0.5 U 0.5 U 1.1 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G64 WB‐02‐I1/I2‐2 2/27/2012 10:59 PDB GW µg/L 0.53 = 0.5 U 0.5 U 0.77 = 0.5 UWB‐02 (I1/I2) I1/I2 F4EI8 WB‐02‐I1/I2‐27‐Q311 8/22/2011 8:55 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐02 (I1/I2) I1/I2 F4EI7 WB‐02‐I1/I2‐22‐Q311 8/22/2011 8:50 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐02 (I1/I2) I1/I2 F4EI5 WB‐02‐I1/I2‐17‐Q311 8/22/2011 8:45 PDB GW µg/L 0.88 LJ 5.0 U 5.0 U 1.1 LJ 2.0 UWB‐02 (I1/I2) I1/I2 F4EI4 WB‐02‐I1/I2‐12‐Q311 8/22/2011 8:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐02 (I1/I2) I1/I2 F4EI9 WB‐02‐I1/I2‐7‐Q311 8/22/2011 8:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 2.1 LJ 2.0 UWB‐02 (I1/I2) I1/I2 F4EI6 WB‐02‐I1/I2‐2‐Q311 8/22/2011 8:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.1 LJ 2.0 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐27‐Q111 WB‐02‐I1/I2‐27 2/16/2011 13:01 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐22‐Q111 WB‐02‐I1/I2‐22 2/16/2011 12:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐17‐Q111 WB‐02‐I1/I2‐17 2/16/2011 12:57 PDB GW µg/L 0.5 = 0.5 U 0.5 U 0.6 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐12‐Q111 WB‐02‐I1/I2‐12 2/16/2011 12:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐7‐Q111 WB‐02‐I1/I2‐7 2/16/2011 12:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐2‐Q111 WB‐02‐I1/I2‐2 2/16/2011 12:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 = 0.5 UWB‐02 (I1/I2) I FGF40 NA 7/27/1999 0:00 unknown GW µg/L 4 = 1 U 0.6 LJ 4 = 1 UWB‐02 (I1/I2) I FQ841 NA 11/3/1997 0:00 unknown GW µg/L 4 = 1 U 1 U 4 = 1 UWB‐02 (I1/I2) I 9705043‐4 NA 5/19/1997 0:00 unknown GW µg/L 3.1 = 1 ND 1 ND 3.4 = ND
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 71 OF 72
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TABLE 3-5Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through August 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2-DCE (cis & trans)
cis-1,2-DCE PCE
trans-1,2-DCE TCE
Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquiferZonea Sample ID Location Date Collected Sampling Method
WB‐02 (S) NA 5/10/2020 0:00 unknownWB‐02 (S) S FQ839 NA 11/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UWB‐02 (S) S 9705043‐3 NA 5/19/1997 0:00 unknown GW µg/L 1 ND 1 ND 1 ND 1 ND ND
5/10/2020 0:00 unknownNotes:µg/L = microgram per literDCE = dichloroethyleneDL = diluted sample; used as suffix to Sample IDGW = groundwaterLFS = low‐flow samplingNA = not applicableND = not detectedM = Reported concentration should be used as a raised quantitation limit because of interferences and/or laboratory contamination.MCL = maximum contaminant levelPCE = perchloroethylene (tetrachloroethylene)PDB = passive diffusion bagTCE = trichloroethyleneU = not detected= = detected concentrationJ = estimated concentrationUJ = not detected, estimated concentration ‐ resulting from improper temperature or holding time exceedanceL = Reported concentration is below the Contract Required Quantitation Limit
* = See Long‐term Monitoring Plan (included in Volume 1 of the 100% Remedial Design) for description of the aquifer zones.** = The Record of Decision does not list a remediation goal for vinyl chloride. Value is the NMED drinking water standard.Bold = detected result
^ = High biased (actual concentration may be lower than the reported)
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐5ES110514201639SPB PAGE 72 OF 72
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TABLE 3‐6Summary of Analytical Results From Recent ASTP Influent Water SamplingFruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Sample ID DateTCE
(µg/L) Qcis 1,2‐DCE
(µg/L) Qtrans 1,2‐DCE
(µg/L) QSeptember 2013FAP SP‐1a N Influent 9/25/13 3.6 1.2 0.5 UFAP SP‐1 DUPa QA/QC Influent 9/25/13 3.1 1.2 0.5 UOctober 2013FAP SP‐1a N Influent 10/28/13 2.7 1.1 0.5 UFAP SP‐1 DUPa QA/QC Influent 10/28/13 2.7 1.1 0.5 UNovember 2013FAP SP‐1a N Influent 11/19/13 2.8 1.1 0.5 UFAP SP‐5b N Effluent 11/19/13 0.5 U 0.5 U 0.5 UDecember 2013FAP SP‐1a N Influent 12/16/13 3.0 1.1 0.5 UFAP SP‐1 DUPa QA/QC Influent 12/16/13 2.9 1.1 0.5 UFAP SP‐5b N Effluent 12/16/13 NA U NA U 0.5 UJanuary 2014FAP SP‐1a N Influent 1/20/14 2.5 1.0 0.5 UFAP SP‐1 DUPa QA/QC Influent 1/20/14 2.6 1.0 0.5 UFAP SP‐5b N Effluent 1/20/14 0.5 U 0.5 U 0.5 UFebruary 2014FAP SP‐1a N Influent 2/17/14 2.4 0.9 0.5 UFAP SP‐1 DUPa QA/QC Influent 2/17/14 2.5 1.0 0.5 UFAP SP‐5b N Effluent 2/17/14 0.5 U 0.5 U 0.5 UMarch 2014FAP SP‐1a N Influent 3/18/14 2.6 1.0 0.5 UFAP SP‐1 DUPa QA/QC Influent 3/18/14 2.4 1.0 0.5 UFAP SP‐5b N Effluent 3/18/14 0.5 U 0.5 U 0.5 UJune 2014FAP SP‐1a N Influent 6/16/14 2.6 1.0 0.5 UFAP SP‐1 DUPa QA/QC Influent 6/16/14 2.5 1.0 0.5 UFAP SP‐5b N Effluent 6/16/14 0.5 U 0.5 U 0.5 UAugust 2014FAP SP‐1a N Influent 8/27/14 3.0 1.1 0.5 UFAP SP‐1 DUPa QA/QC Influent 8/27/14 3.0 1.2 0.5 UFAP SP‐5b N Effluent 8/27/14 0.5 U 0.5 U 0.5 UNotes:a Sample taken from sample port at ASTP influent line (SP‐1). Data Qualifier (Q):b Sample taken from sample port after treated water bag filter (SP‐5).c Results reported are from reanalysis, see text for discussion L = The reported concentration is µg/L = micrograms per literASTP = air stripper treatment plant J = Estimated valueCRQL = Contract‐required quantitation limit U = The analyte was not detectedDUP = field duplicate sampleFAP = Fruit Avenue PlumeN = normal sample. QA/QC = quality assurance and quality control sampleOnly analytical results for contaminants of concern are included in this table.
Sample Typeand Location
below the CRQL
FAP_2014 ANNUAL GW SAMPLING REPORT_TABLE 3‐6ES110514201639SPB PAGE 1 OF 1
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Figures
011443
FIGURES
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FAP_2014_ANNUAL GW SAMPLING REPORTT_FIGURES ES110514201639SPB
011444
R:\FRUITAVENUE_345406\MAPFILES\AUG_2014\SITE_MAP_AUG_2014.MXD FLONDON 10/15/2014 5:51:57 PM
FIGURE 2-1LTM Program, Monitor Well LocationsFruit Avenue Plume Superfund SiteAlbuquerque, NM
Legend
Presumed Source Area
Extraction Well
Air Stripper Treatment Plant
Injection Well
RailroadMonitor Wells
pruc
e S
t
Silver Ave
Copper Ave
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
Silver Ave
Marquette Pl
Granite AveMarble Ave
Oak
St
Syc
Map
le S
t
Spru
ce S
t
Hig
h S
t
Gold Ave
Legion
Tijeras Ave
Luna
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Manzano Ct
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
cam
ore
St
SpruceS
7th
St
Ced
ar S
t
Edith
Blvd
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
8th
St
Enci
no P
l
7th
St
Tijeras Ave
Iron Ave
1st S
3rd
S t
4th
St
St
11th
St
Fruit Ave Lomas Blvd
5th
St
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank DM-01
(S)
DM-05 (S)
DM-06(I1/I2)
DM-07(I1/I2)
DM-08(I1/I2)
DM-09 (S)
DM-10(S)
DM-11(S)
DM-12(I1/I2)
DM-13(S/I1/I2/D1)
HSM-I2-4(I2)
HSM-I2-5 (I2)
McDonald’s(D2)
MNW-1(I2)
MNW-10 (I1/I2)
MNW-11(I1/I2/D1/D2)
MNW-12(I1/I2/D1/D2)
MNW-13(D1/D2/D3/D4)
MNW-14(I2/D1/D2)
MNW-2(I2)
MNW-3 (D1/D2/D3)
MNW-4(D1/D2/D3)
MNW-5(D1/D2/D3/D4)
MNW-6(D1/D2/D3)
MNW-7(D4)
MNW-8 (I1)
MNW-8(I2)
MNW-9(I1/I2/D1/D2)
SFMW-01(S)
SFMW-03 (S)
SFMW-07 (S)
SFMW-10 (I2)SFMW-11(S)
SFMW-12(I1)
SFMW-13 (I2)
SFMW-14 (D1) SFMW-15 (S)
SFMW-16(I1)
SFMW-17 (I2)
SFMW-18 (I1)
SFMW-20(I1)
SFMW-21(I2)
SFMW-22 (D1)SFMW-23 (D2)
SFMW-24(S) SFMW-25
(I1/I2)
SFMW-26(I2)
SFMW-27 (I2)
SFMW-28(I2)
SFMW-31 (I2)
SFMW-32 (I2)
SFMW-33(D2)
SFMW-34(D4)
SFMW-35(D3)
SFMW-36(D4)
SFMW-37(I2)
SFMW-38(D1)
SFMW-39(D2)
SFMW-40(D3)
SFMW-41(D3/D4)
SFMW-43(I1)
SFMW-44(D2)
SFMW-45(D2)
SFMW-46(D1/D2)
SFMW-47(I1/I2)
SPSC-MW19(S)
SPSC-MW5 (S)
SPSC-W13(S)
MNW-15(D1/D2/D3)
WB-01(I1/I2)
WB-02 (I1/I2)
MNW-16(D1/D2/D3/D4)
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
?
? 5
5
5
5
5
?
I2/D1E-I1 D2E-I3 D2E-P1
0 300 600150 Feet
TCE Composite Plume Boundary at 5 μg/L - August 25, 2014
Upgradient Off-Site TCE Composite Plume Boundary at 5 μg/L - August 25, 2014
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011445
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-01 (S)4922.40
DM-05 (S)4921.77
DM-09 (S)4919.78
DM-10 (S)4918.04
DM-11 (S)4925.27
DM-13 (S)4921.52
SFMW-01 (S)4923.24
SFMW-03 (S)4921.72
SFMW-07 (S)4923.78
SFMW-11 (S)4927.11
SFMW-15 (S)4920.34
SFMW-24 (S)4919.80
SPSC-MW19 (S)4913.55
SPSC-MW5 (S)4918.06
SPSC-W13 (S)4912.67
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4925
49154920
I2/D1E-I1
D2E-I3D2E-P1
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_S.MXD FLONDON 10/6/2014 11:42:43 AM
LegendS Zone Monitor WellOther Site Monitor WellExtraction WellAir Stripper Treatment PlantInjection WellWater Level Elevation Contour - (Dashed Where Inferred)
Inferred Direction of Groundwater FlowRailroadPipelinesPresumed Source Area
0 300 600150 Feet
Notes1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 3-1Distribution of Water Levelsin the Shallow Aquifer Zone August 24 2014Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011446
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-06 (I1/I2)4916.88
DM-07 (I1/I2)4917.53
DM-08 (I1/I2)4918.04
DM-12 (I1/I2)4926.22
DM-13 (I1)4922.27
MNW-10 (I1)4928.75
MNW-11 (I1)4933.73
MNW-12 (I1)4933.82 MNW-8 (I1)
4930.37
MNW-9 (I1)4933.68
SFMW-12 (I1)4927.16
SFMW-16 (I1/I2)4921.07
SFMW-18 (I1/I2)4924.16
SFMW-20 (I1/I2)4912.06
SFMW-25 (I1/I2)4918.78
SFMW-43 (I1/I2)4904.52
SFMW-47 (I1/I2)4922.07
WB-01 (I1/I2)4927.86
WB-02 (I1/I2)4928.96
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4915
4910 4905
4930
4920
4925
I2/D1E-I1D2E-I3
D2E-P1
LegendI1 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Water Level Elevation Contour - (Dashed Where Inferred)
Inferred Direction of Groundwater Flow
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_I1.MXD FLONDON 10/6/2014 11:50:56 AM
0 300 600150 Feet
Notes1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 3-2Distribution of Water Levelsin the I1 Aquifer Zone August 24 2014Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011447
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-06 (I1/I2)4916.88
DM-07 (I1/I2)4917.53
DM-08 (I1/I2)4918.04
DM-12 (I1/I2)4926.22
DM-13 (I2)4923.17
HSM-I2-4 (I2)4926.00
HSM-I2-5 (I2)4924.50
MNW-1 (I2)4929.96
MNW-10 (I2)4928.79
MNW-11 (I2)4933.75
MNW-12 (I2)4933.80
MNW-14 (I2)4927.13
MNW-2 (I2)4925.68
MNW-8 (I2)4930.57
MNW-9 (I2)4931.88
SFMW-10 (I2)4925.84
SFMW-13 (I2)4927.18
SFMW-16 (I1/I2)4921.07
SFMW-17 (I2)4922.43SFMW-18 (I1/I2)
4924.16
SFMW-20 (I1/I2)4912.06
SFMW-21 (I2)4912.23
SFMW-25 (I1/I2)4918.78
SFMW-26 (I2)4918.39
SFMW-27 (I2)4926.44
SFMW-28 (I2)NA SFMW-29 (I2)
NA
SFMW-31 (I2)4904.82
SFMW-32 (I2)4905.84
SFMW-37 (I2)4914.75
SFMW-43 (I1/I2)4904.52
SFMW-47 (I1/I2)4922.07
WB-01 (I1/I2)4927.86
WB-02 (I1/I2)4928.96
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4915
4910
4905
4930
49204925
I2/D1E-I1
D2E-I3
D2E-P1
LegendI2 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour - (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_I2.MXD FLONDON 11/3/2014 4:58:48 PM
0 300 600150 Feet
Notes1. Water levels are in feet above Mean Sea Level (MSL).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation
with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumedbased on homogeneous and isotropic conditions.
4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 3-3Distribution of Water Levelsin the I2 Aquifer Zone August 24 2014 Fruit Avenue Plume Superfund Site Albuquerque, NM
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011448
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-13 (D1)4925.84
MNW-11 (D1)4933.73
MNW-12 (D1)4933.83
MNW-13 (D1)4906.42
MNW-14 (D1)4928.76
MNW-3 (D1)4914.78
MNW-4 (D1)4905.62
MNW-5 (D1)4909.81
MNW-6 (D1)4911.88
MNW-9 (D1)4931.75
SFMW-14 (D1)4927.39
SFMW-22 (D1)4912.58
SFMW-38 (D1)4908.28
SFMW-46 (D1/D2)4905.98
MNW-15 (D1)4893.05
MNW-16 (D1)4906.47
4930
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4925
4920
4915
4910
4905
4900 4895
I2/D1E-I1
D2E-I3
D2E-P1
LegendD1 Zone Monitor Well
Other Site Monitor Well
Air Stripper Treatment Plant
Injection Well
Extraction Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D1.MXD FLONDON 11/3/2014 4:59:49 PM
FIGURE 3-4Distribution of Water Levelsin the D1 Aquifer Zone August 24 2014Fruit Avenue Plume Superfund SiteAlbuquerque, NM
0 300 600150 Feet
Notes1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011449
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
McDonald’s (D2)4914.21
MNW-11 (D2)4933.71
MNW-12 (D2)4933.79
MNW-13 (D2)4906.65
MNW-14 (D2)4929.11
MNW-3 (D2)4913.60
MNW-4 (D2)4905.88
MNW-5 (D2)4910.11
MNW-6 (D2)4911.99
MNW-9 (D2)4931.91
SFMW-23 (D2)4912.26
SFMW-33 (D2)4915.06
SFMW-39 (D2)4908.19
SFMW-44 (D2)4909.51
SFMW-45 (D2)4908.78
SFMW-46 (D1/D2)4905.98
MNW-15 (D2)4902.97
MNW-16 (D2)4907.02
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4915
4910
4905
4930
4920
4925 I2/D1E-I1
D2E-I3
D2E-P1
LegendD2 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour - (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D2.MXD FLONDON 10/6/2014 1:49:23 PM
0 300 600150 Feet
Notes1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 3-5Distribution of Water Levelsin the D2 Aquifer Zone August 24 2014Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011450
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
MNW-13 (D3)4907.15
MNW-3 (D3)4912.64
MNW-4 (D3)4906.31
MNW-5 (D3)4910.30
MNW-6 (D3)4912.08
SFMW-35 (D3)4911.09
SFMW-40 (D3)4907.59
SFMW-41 (D3/D4)4907.03
MNW-15 (D3)4903.15
MNW-16 (D3)4907.25
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4905
4910
I2/D1E-I1
D2E-I3
D2E-P1
LegendD3 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour - (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
Notes1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D3.MXD FLONDON 10/7/2014 7:57:48 AM
0 300 600150 Feet
FIGURE 3-6Distribution of Water Levelsin the D3 Aquifer Zone August 24 2014Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011451
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
MNW-13 (D4)4907.66
MNW-5 (D4)4910.38
MNW-7 (D4)4909.98
SFMW-34 (D4)4910.99
SFMW-36 (D4)4910.11
SFMW-41 (D3/D4)4907.03
MNW-16 (D4)4907.62
4910
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4910
I2/D1E-I1
D2E-I3
D2E-P1
LegendD4 Zone Monitor Well
Other Site Monitor Well
Air Stripper Treatment Plant
Injection Well
Extraction Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D4.MXD FLONDON 11/3/2014 5:01:39 PM
0 300 600150 Feet
Notes1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 3-7Distribution of Water Levelsin the D4 Aquifer Zone August 24 2014Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011452
4870
4880
4890
4900
4910
4920
4930
4940
2004 2005 2006 2008 2009 2010 2012 2013 2014 2016
Gro
undw
ater
Ele
vaon
( M
SL)
DM-01 (S)
DM-04 (S)
DM-05 (S)
DM-09 (S)
DM-10 (S)
DM-11 (S)
DM-13 (S)
SFMW-01 (S)
SFMW-02 (S)
SFMW-03 (S)
SFMW-04 (S)
SFMW-05 (S)
SFMW-07 (S)
SFMW-11 (S)
SFMW-24 (S)
SPSC-MW19 (S)
SPSC-MW5 (S)
SPSC-W13 (S)
WB-01 (S)
ES110514201639SPB
FIGURE 3-8 Shallow Aquifer Zone - Groundwater Eleva on Trends over Time, February 2002 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
011453
4870
4880
4890
4900
4910
4920
4930
4940
2001 2004 2006 2009 2012 2014 2017
Gro
undw
ater
Ele
vaon
( M
SL)
DM-02 (I1)
DM-03 (I1)
DM-06 (I1)
DM-07 (I1)
DM-08 (I1)
SFMW-20 (I1)
SFMW-25 (I1)
SFMW-47 (I1)
MNW-9 (I1)
MNW-11 (I1)
MNW-12 (I1)
MNW-8 (I1)
MNW-10 (I1)
ES110514201639SPB
FIGURE 3-9I1 Aquifer Zone - Groundwater Eleva on Trends over Time, February 2002 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
011454
ES110514201639SPB
FIGURE 3-10I2 Aquifer Zone - Groundwater Eleva on Trends over Time, February 2002 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
4870
4880
4890
4900
4910
4920
4930
4940
2001 2004 2006 2009 2012 2014 2017
Gro
undw
ater
Ele
vaon
( M
SL)
HSM-I2-5 (I2)
MNW-1 (I2)
MNW-11 (I2)
MNW-14 (I2)
MNW-9 (I2)
SFMW-17 (I2)
SFMW-21 (I2)
SFMW-25 (I2)
SFMW-26 (I2)
SFMW-32 (I2)
SFMW-47 (I2)
011455
ES110514201639SPB
FIGURE 3-11D1 Aquifer Zone - Groundwater Eleva on Trends over Time, February 2002 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
4870
4880
4890
4900
4910
4920
4930
4940
2001 2004 2006 2009 2012 2014 2017
Gro
undw
ater
Ele
vaon
( M
SL)
MNW-11 (D1)
MNW-12 (D1)
MNW-13 (D1)
MNW-15 (D1)
MNW-4 (D1)
MNW-5 (D1)
MNW-9 (D1)
SFMW-22 (D1)
SFMW-38 (D1)
SFMW-46 (D1)
011456
ES110514201639SPB
FIGURE 3-12D2 Aquifer Zone - Groundwater Eleva on Trends over Time, February 2002 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
4870
4880
4890
4900
4910
4920
4930
4940
2001 2004 2006 2009 2012 2014 2017
Gro
undw
ater
Ele
vaon
( M
SL)
McDonald's (D2)
MNW-15 (D2)
MNW-5 (D2)
SFMW-23 (D2)
SFMW-39 (D2)
SFMW-44 (D2)
SFMW-45 (D2)
SFMW-46 (D2)
MNW-9 (D2)
MNW-4 (D2)
MNW-11 (D2)
MNW-12 (D2)
MNW-3 (D2)
011457
ES110514201639SPB
FIGURE 3-13D3 Aquifer Zone - Groundwater Eleva on Trends over Time, February 2002 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
4870
4880
4890
4900
4910
4920
4930
4940
2001 2004 2006 2009 2012 2014 2017
Gro
undw
ater
Ele
vaon
( M
SL)
MNW-15 (D3)
MNW-5 (D3)
SFMW-35 (D3)
SFMW-40 (D3)
MNW-13 (D3)
MNW-3 (D3)
MNW-4 (D3)
MNW-6 (D3)
011458
ES110514201639SPB
FIGURE 3-14D4 Aquifer Zone - Groundwater Eleva on Trends over Time, February 2002 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
4870
4880
4890
4900
4910
4920
4930
4940
2001 2004 2006 2009 2012 2014 2017
Gro
undw
ater
Ele
vaon
( M
SL)
MNW-5 (D4)
MNW-13 (D4)
SFMW-34 (D4)
SFMW-36 (D4)
011459
This page intentionally left blank.
011460
R:\FRUITAVENUE_345406\MAPFILES\AUG_2014\FA_TCE_I1.MXD FLONDON 11/3/2014 4:46:45 PM
FIGURE 3-15
Distribution of Chlorinated Volatile Organic Compounds
in the I1 Aquifer Zone August 25 2014
Fruit Avenue Plume Superfund Site
Albuquerque, NM
Legend
@A Other Site Monitor Well
Presumed Source Area! Extraction Well
" Air Stripper Treatment Plant
! Injection Well
Railroad@A I1 Zone Monitor Well - Sample Aug. 2014
TCE concentration contour
(dashed where inferred)
"
!
!
!!
Granite Ave
Silver Ave
Copper Ave
Tijeras Ave
Don C
iprian
oC
t
Slate Ave
11th
St
Marquette Pl
Granite AveMarble Ave
Oak S
t
Syc
amo
Forr
este
r A
ve
Maple
St
Spru
ce S
t
Legion R
Tijeras Ave
Lun
aB
l vd
1st S
t
Elm
St
Gold Ave
6th
St
Medical A
rtsAve
Rid
ge P
l
Slate Ave
Page Ave
Manzano Ct
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Ke
leh
er
Ave
Spruce
St
7th
St
Ce
da
r S
t
Edith
Blv
d
Hig
h S
t
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
8t h
St
Encin
o P
l
7th
St
Tijeras Ave
1st S
t
3rd
St
4th
St
11th
St
Fruit Ave
12th
St
Wa
Lomas Blvd
5th
St
Silver Ave
Mulb
err
y S
t
Slate Ave
Marquette Ave
Edith B
lvd
Central Ave
Dr Martin Luther King Jr Ave
Tra
nq
uil i
no
Ct
Marble Ave
Inte
r sta
te 2
5
6th
St
Lomas Blvd
Lead Ave
SH
47
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank @A
@A
@A
@A@A@A@A @A
@A
@A
@A@A
@A
@A@A
@A@A@A@A
@A@A
@A
@A
@A@A
@A
@A@A @A@A
@A
@A@A@A
@A@A@A@A@A
@A@A@A@A@A
@A@A@A@A@A
@A@A@A@A
@A
@A@A@A@A
@A@A@A@A
@A@A@A@A@A
@A@A@A@A
@A
@A@A@A
@A@A@A@A@A@A
@A
@A
@A
@A@A
@A@A
@A
@A@A@A
@A@A@A
@A @A@A@A
@A@A
@A@A@A@A@A@A@A
@A
@A
@A
@A
@A
@A
@A@A @A@A
@A
@A@A@A@A
@A
@A@A
@A
@A
@A
@A
@A
@A@A
@A
@A
@A
@A
@A
@A
@A@A@A@A
@A@A
@A
@A
@A
@A
@A@A
@A
@A
@A@A@A@A
@A@A
@A
@A
@A@A
@A
@A
@A
@A@A
@A
@A
@A
@A@A
@A
@A@A
@A
@A
@A
@A@A
@A
@A
@A@A
@A
@A
@A
@A
SFMW-18 (I1)PCE 0.5 UTCE 2.4cis-DCE 1.1trans-DCE 0.5 UVC 0.5 U
SFMW-20 (I1)
PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-47 (I1/I2)PCE 0.5 UTCE 25.2cis-DCE 6.2trans-DCE 0.9VC 0.5 U
SFMW-25 (I1)PCE 0.5 UTCE 7.9cis-DCE 3.3trans-DCE 0.7VC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
5
15
10
I2/D1E-I1
D2E-I3
D2E-P1
0 300 600150 Feet
$I1 Zone Monitoring Well – Not Sampled@A
Aquifer Zones:
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)
I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amsl
I2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amsl
D1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amsl
D2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amsl
D3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amsl
D4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
Volatile Organic Compounds:
Tetrachloroethene (PCE)
Trichloroethene (TCE)
Cis-1,2-dichloroethene (cis-DCE)
Trans-1,2-dichloroethene (trans-DCE)
Vinyl chloride (VC)
Units: micrograms per liter (μg/L)
Qualifers: J - estimated
U - not detected
JL - Estimated Concentration
= - detected concentration
NA – Not Analyzed
Notes:
1) TCE concentration contours based on analytical
results from August 25, 2014 sample event,
and historical data.
2) PDB – Passive diffusion bag depth interval
Date 2004 2005 2006 2007 2008 April 2009 Oct 2009 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug-14
PCE 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 5.0 U 0.5 U 0.52 = 0.5 U 0.5 U 0.5 U
TCE 56 J 65 J 28 = 37 JL 33 = 23.4 J 16 = 18.4 = 20 = 15 = 15 = 19 = 20.9 = 20.6 = 25.2
cis-DCE 7.8 = 10 = 5.6 = 6.5 JL 6.8 = 5.0 J 3.7 = 4.2 = 5.6 = 3.4 = 4.5 = 6.4 = 5.2 = 2.3 = 6.2
trans-DCE 1.3 = 1.9 = 1 = 1.1 JL 1.1 = 0.8 J 0.57 = 0.7 = 5.0 U 0.52 = 0.52 = 1.1 = 0.6 = 0.7 = 0.9
VC 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.64 = 0.5 U 0.5 U 0.5 U
SFMW-47 (I1/I2)
Date 2004 2005 2006 2007 2008 April 2009 Oct 2009 Feb 2010 Aug 2010 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.034 JL 0.5 U 0.5 U 0.5 U 0.5 U
TCE 18 = 25 J 17 = 15.4 JL 13 = 11.8 = 10 = 9.6 J 9.9 = 11 = 14 = 9.4 = 8.7 = 8.9 = 7.7 = 4.6 = 7.9
cis-DCE 6.5 = 8.8 J 6.3 = 6 JL 6.1 = 4.6 J 3.7 = 4 = 3.9 = 3.6 = 5.2 = 3 = 3.6 = 3.9 = 3.2 = 2.3 = 3.3
trans-DCE 1.6 = 2.5 J 1.6 = 1.9 JL 2.3 = 1.1 J 0.79 = 0.80 = 0.70 = 0.60 = 5.0U 0.58 = 0.65 = 0.76 = 0.7 = 0.9 = 0.7
VC 0.5U 0.14 JL 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5 U 0.5 U 0.5 U 0.5 U
SFMW-25(I1)
011461
R:\FRUITAVENUE_345406\MAPFILES\AUG_2014\FA_TCE_I2.MXD FLONDON 11/3/2014 4:40:45 PM
Aquifer Zones:
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)
I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amsl
I2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amsl
D1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amsl
D2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amsl
D3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amsl
D4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
Volatile Organic Compounds:
Tetrachloroethene (PCE)
Trichloroethene (TCE)
Cis-1,2-dichloroethene (cis-DCE)
Trans-1,2-dichloroethene (trans-DCE)
Vinyl chloride (VC)
FIGURE 3-16
Distribution of Chlorinated Volatile Organic Compounds
in the I2 Aquifer Zone August 25 2014
Fruit Avenue Plume Superfund Site
Albuquerque, NM
Legend
@A Other Site Monitor WellPresumed Source Area
! Extraction Well
" Air Stripper Treatment Plant
! Injection Well
Railroad@A I2 Zone Monitor Well - Sampled Aug. 2014
TCE concentration contour
(dashed where inferred)
Units: micrograms per liter (μg/L)
Qualifers: J - estimated
U - not detected
JL - Estimated Concentration
= - detected concentration
NA – Not Analyzed
"
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Silver Ave
Copper Ave
Tijeras Ave
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Silver Ave
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Granite AveMarble Ave
Oak S
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Hig
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Gold Ave
Legion R
Tijeras Ave
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5th
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Gold Ave
6t h
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Medical A
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Slate Ave
Page Ave
Manzano Ct
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Ke
leh
er
Ave
Sycam
ore
St
Spruce
St
7th
St
Ce
da
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t
Edith
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Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd S
t
Roma Ave
Gold Ave
8t h
St
Encin
o P
l
7th
St
jeras Ave
Iron Ave
1st S
t
3rd
St
4th
St
Arn
o S
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11th
St
Fruit Ave Lomas Blvd
5th
St
Silver Ave
Mulb
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Slate Ave
Marquette Ave
Ed
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Dr Martin Luther King Jr Ave
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WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer Plaza
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HSM-I2-5 (I2)
PCE 0.5 UTCE 26.0cis-DCE 6.9trans-DCE 1.1VC 0.5 U
MNW-1 (I2)PCE 0.5 U
TCE 19.7cis-DCE 4.3trans-DCE 1.3VC 0.5 U
MNW-14 (I2)PCE 0.5 UTCE 44.8cis-DCE 7.9trans-DCE 1.3VC 0.5 U
MNW-8 (I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-9 (I2)PCE 0.5 UTCE 2.8
cis-DCE 1.4trans-DCE 0.5 UVC 0.5 U
SFMW-17 (I2)
PCE 0.5 UTCE 5.6cis-DCE 3.8trans-DCE 3.2VC 0.5 U
SFMW-21 (I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-26 (I2)PCE 0.5 UTCE 2.6cis-DCE 1.2trans-DCE 0.5 UVC 0.5 U
SFMW-27 (I2)
PCE 0.5 UTCE 14.5cis-DCE 6.1trans-DCE 4.3VC 0.5 U
SFMW-47 (I1/I2)PCE 0.5 UTCE 25.2cis-DCE 6.2trans-DCE 0.9VC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
20
10
5 I2/D1E-I1
D2E-I3
D2E-P1
0 300 600150 Feet
$I2 Zone Monitoring Well – Not Sampled@A
Event 2009 Q1 2009 Q3 2010 Q1 2010 Q3 2011 Q1 2011 Q3 2012 Q1 2012 Q3 2013 Q1 2013 Q3 Feb 2014 Aug 2014
PDB* 7 7 7 7 7 7 7 7 7 7 7 7
PCE 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 0.5 U 1.0 U 0.5 U 0.5 U 0.5 U 0.5 U
TCE 12.7 = 8.4 = 8.4 = 10.2 = 10.7 JH 15 = 14 = 17 = 13 = 22.4 = 19 = 19.7
cis-DCE 2.3 = 1.7 = 1.9 = 2.0 = 1.9 = 2.9 LJ 2.6 = 3.4 = 2.7 = 3.7 = 4.1 = 4.3
trans-DCE 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 0.5 U 0.29 LJ 0.22 LJ 0.6 = 1 = 1.3
VC 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 1.0 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW-1 (I2)
Event 2009 Q1 2009 Q3 2010 Q1 2010 Q3 2011 Q1 2011 Q3 2012 Q1 2012 Q3 2013 Q1 2013 Q3 Feb 2014 Aug 2014
PDB* 17 17 17 17 17 17 17 17 17 17 17 17
PCE 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 0.5 U 1.0 U 0.5 U 0.5 U 0.5 U 0.5 U
TCE 42.7 = 29 = 31.2 = 21 = 25.6 = 31 = 20 = 32 = 20 = 23.2 = 17.9 = 26
cis-DCE 6.8 = 5.4 = 6 = 5.3 = 5.2 = 6.9 = 5 = 5.7 = 6.1 = 6.2 = 5.9 = 6.9
trans-DCE 1.2 = 1.1 = 1.2 = 1.3 = 0.6 = 1.1 LJ 0.73 = 0.65 LJ 0.81 = 0.9 = 0.8 = 1.1
VC 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 1.0 U 0.5 U 0.5 U 0.5 U 0.5 U
HSM-I2-5 (I2)
Event 2013 Q1 Aug 2014
PDB* 2 8 2 8 2 8 2 8 2 8 2 8 8 2 8
PCE 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 5.0 U 0.5 U 0.15 LJ 0.17 LJ 22 J 0.16 LJ 0.13 LJ 0.13 LJ 0.5 U 0.5 U 0.5 U
TCE 4.1 = 0.5 U 3.8 = 4.5 = 4.6 LJ 5.2 = 3.1 = 3.7 = 3.0 = 110 J 3.1 = 3.1 = 2.9= 0.6 = 2.2 = 2.6
cis-DCE 2.2 = 0.5 U 1.7 = 1.8 = 2.5 LJ 2.5 LJ 1.4 = 1.4 = 1.6 = 0.29 LJ 1.6 = 1.5 = 1.4 = 0.8 = 1.2 = 1.2
trans-DCE 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 5.0 U 0.1 LJ 0.11 LJ 0.11 LJ 0.062 LJ 0.5 U 0.12 LJ 0 = 0.5 U 0.5 U 0.5 U
VC 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
SFMW-26 (I2)
2012 Q1 Feb 20142013 Q12010 Q3 2011 Q1 2012 Q32011 Q3
Event Aug 2014
PDB* 2 8 2 8 2 8 2 8 2 8 2 8 2 8 2 8
PCE 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 5.0 U 0.5 U 0.5 U 2.5 U 0.16 LJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
TCE 32.1 = 30.0 = 32.1 = 26.2 = 44 = 51 = 39 = 35 = 46 = 48 = 33 = 39 = 36.8 = 42.8 = 32.4 = 38.2 = 44.8
cis-DCE 8.8 = 8.2 = 7.4 = 6.5 = 11 = 9.7 = 8.6 = 7.8 = 8.1 = 7.6 = 9.2 = 8.8 = 8.4 = 7.7 = 7.6 = 7.7 = 7.9
trans-DCE 1.1 = 1.2 = 0.8 = 2 = 1.3 LJ 5.0 U 3 = 0.93 = 0.69 LJ 0.70 LJ 0.99 = 0.85 = 1.1 = 0.9 = 1.1 = 1.1 = 1.3
VC 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 2.0 U 0.5 U 0.5 U 2.5 U 2.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW-14 (I2)
2012 Q3 Feb 20142011 Q1 2013 Q1 2013 Q32010 Q3 2011 Q3 2012 Q1
Event 2011 Q1 2011 Q3 2012 Q1 2012 Q3 2013 Q1 2013 Q3 Feb 2014 Aug 2014
PDB* 8 8 8 8 8 8 8 8
PCE 0.5 U 5.0 U 0.5 U 0.031 LJ 0.5 U 0.5 U 0.5 U 0.5 U
TCE 8.4 = 13 = 9.1 = 9.9 = 9.8 = 11.3 = 13.4 = 14.5
cis-DCE 6.4 = 6.7 = 4.6 = 4.9 = 6.3 = 5.4 = 4.9 = 6.1
trans-DCE 5.3 = 4.7 LJ 3.9 = 3.4 = 5.6 = 4.4 = 2.5 = 4.3
VC 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
SFMW-27 (I2)
Notes:
1) TCE concentration contours based on analytical
results from August 25, 2014 sample event,
and historical data.
2) PDB – Passive diffusion bag depth interval
011462
R:\FRUITAVENUE_345406\MAPFILES\AUG_2014\FA_TCE_D1.MXD FLONDON 11/5/2014 7:16:04 AM
FIGURE 3-17
Distribution of Chlorinated Volatile Organic Compounds
in the D1 Aquifer Zone August 25 2014
Fruit Avenue Plume Superfund Site
Albuquerque, NM
"
!
!
!
Sp
ruce S
t
Silver Ave
Copper Ave
11t h
St
Tijeras Ave
Do
n C
ipri
ano
Ct
Slate Ave
Silver Ave
Marquette Pl
Oak S
t
Map
le S
t
Sp
ruce S
t
Hig
h S
t
Gold Ave
Tijeras Ave
Lun
aB
l vd
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical A
rtsAve
Rid
ge P
l
Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Ke
leh
er
Ave
Sycam
ore
St
S
7th
St
Ce
dar
St
Edith
Blv
d
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7t h
St
Tijeras Ave
Iron Ave
3rd
St
4th
St
Arn
o S
t
11th
St
Fruit Ave Lomas Blvd
5th
St
Lead Ave
10th
St
Silver Ave
Mulb
err
y S
t
Slate Ave
Marquette Ave
Ed
ith B
lvd
Central Ave
Dr Martin Luther King Jr Ave
Tra
nquil i
no C
t
Marble Ave
Inte
r sta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH
47
SH
47
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WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
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MNW-11 (D1)PCE 0.5 UTCE 29.0
cis-DCE 11.3trans-DCE 12.8VC 0.5 U
MNW-14 (D1)PCE 0.5 UTCE 1.6cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-5 (D1)PCE 1.4TCE 9.7cis-DCE 5.6trans-DCE 2.3VC 0.5 U
MNW-9 (D1)PCE 0.5 UTCE 3.6cis-DCE 1.3trans-DCE 1.0VC 0.5 U
SFMW-14 (D1)PCE 0.5 UTCE 18.8cis-DCE 1.0trans-DCE 0.6VC 0.5 U
SFMW-22 (D1)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-46 (D1/D2)PCE 0.5 UTCE 1.2cis-DCE 1.2trans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
5
10
5I2/D1E-I1
D2E-I3
D2E-P1
0 300 600150 Feet
$Legend
@A Other Site Monitor Well
Presumed Source Area! Extraction Well
" Air Stripper Treatment Plant
! Injection Well
Railroad@A D1 Zone Monitor Well - Sample Aug. 2014
TCE concentration contour
(dashed where inferred)D1 Zone Monitoring Well – Not Sampled@A
Aquifer Zones:
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)
I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amsl
I2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amsl
D1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amsl
D2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amsl
D3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amsl
D4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
Volatile Organic Compounds:
Tetrachloroethene (PCE)
Trichloroethene (TCE)
Cis-1,2-dichloroethene (cis-DCE)
Trans-1,2-dichloroethene (trans-DCE)
Vinyl chloride (VC)
Units: micrograms per liter (μg/L)
Qualifers: J - estimated
U - not detected
JL - Estimated Concentration
= - detected concentration
NA – Not Analyzed
Date 2004 2005 2006 2007 2008 April 2009 Oct 2009 Feb 2010 Aug 2010 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE NA 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
TCE NA 25 = 32 = 28.1 = 35 = 33.1 = 25 = 33.6 = 31 = 35.2 = 46 = 27 = 46 = 36 = 34.8 = 23.4 = 29
cis-DCE NA 4.4 = 4.6 = 6.8 = 7.1 = 6.8 = 6.9 = 7.2 = 5.9 = 8 = 10 = 6.3 = 11 = 11 = 8.9 = 10.2 = 11.3
trans-DCE NA 0.22 LJ 0.68 = 4.2 = 4.8 = 3.8 = 3.7 = 4.1 = 3.8 = 5.6 J 6.6 = 4.2 = 5.6 = 9.3 = 6.2 = 11.8 = 12.8
VC NA 0.12 LJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.14 LJ 0.5 U 0.5 U 0.5 U
MNW-11 (D1)
Date 2004 2005 2006 2007 2008 April 2009 Oct 2009 Feb 2010 Aug 2010 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE 0.81 J 0.6 = 0.5 U 0.5 UJ 0.71 = 0.5 = 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 0.69 = 0.87 = 1.1 = 1.4 = 1.2 = 1.4
TCE 18 J 12 = 9.2 = 9.7 JL 19 = 7.2 = 5.5 = 4.9 = 4.1 = 5.2 = 8.4 = 6.9 = 7.7 = 8.4 = 9 = 8.9 = 9.7
cis-DCE 15 J 10 = 6.7 = 6 JL 12 = 4.6 = 4.2 = 3.5 = 2.9 = 3.6 = 5.3 = 4 = 5.2 = 5.8 = 5.4 = 5.6 = 5.6
trans-DCE 6 J 3.8 = 2.8 = 2.9 JL 4.9 = 2.0 = 2 = 1.8 = 1.5 = 1.6 = 2.0 LJ 1.4 = 1.7 = 2.1 = 2.3 = 2.2 = 2.3
VC 0.5 UJ 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW-5 (D1)
Date 2004 2005 2006 2007 2008 April 2009 Oct 2009 Feb 2010 Aug 2010 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE NA 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 5.0 U 0.5 U 0.048 LJ 0.5 U 0.5 U 0.5 U 0.5 U
TCE NA 15 = 4.2 = 8.8 = 5.6 = 5.2 J 5.2 = 3.4 = 4.8 = 3.4 = 5.7 = 2.3 = 4.6 J^ 2.9 = 3.1 = 3.1 = 3.6
cis-DCE NA 3.4 = 0.69 = 3.8 = 2.3 = 1.2 J 1.2 = 0.8 = 1 = 0.7 = 1.7 LJ 0.57 = 0.92 = 0.83 = 1.3 = 1 = 1.3
trans-DCE NA 0.13 LJ 0.5 U 4 = 2.1 = 0.7 J 0.62 = 0.6 = 0.42 LJ 0.5 U 1.6 LJ 0.29 LJ 0.53 = 0.56 = 1.9 = 0.6 = 1.0
VC NA 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW-9 (D1)
Date 1997 1999 July 2010 Aug 2010 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE 1 U 1 U 0.5 U 0.5 U 0.5 U 5.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
TCE 1 U 1 U 9.4 = 8.2 = 4.6 = 8.5 = 8.7 = 17 = 13 = 18.3 = 14.8 = 18.8
cis-DCE 1 U 1 U 1.3 = 1.0 = 0.5 U 5.0 U 0.65 = 0.84 = 0.94 = 0.9 = 0.8 = 1.0
trans-DCE 1 U 1 U 0.39 LJ 0.5 U 0.5 U 5.0 U 0.5 U 0.24 LJ 0.29 LJ 0 = 0.5 U 0.6
VC 1 U 1 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
SFMW-14 (D1)
Notes:
1) TCE concentration contours based on analytical
results from August 25, 2014 sample event,
and historical data.
2) PDB – Passive diffusion bag depth interval
011463
R:\FRUITAVENUE_345406\MAPFILES\AUG_2014\FA_TCE_D2.MXD FLONDON 11/3/2014 4:40:28 PM
FIGURE 3-18
Distribution of Chlorinated Volatile Organic Compounds
in the D2 Aquifer Zone August 25 2014
Fruit Avenue Plume Superfund Site
Albuquerque, NM
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Sp
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Silver Ave
Ash
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Copper Ave
Tijeras Ave
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Slate Ave
Silver Ave
Marquette Pl
Oak S
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Map
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Hig
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Gold Ave
Tijeras Ave
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Elm
St
5th
St
Gold Ave
6th
St
Medica
l Arts
Ave
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Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Ke
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Ave
Sycam
ore
St
Spr
7th
St
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Edith
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9th
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Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7th
St
Tijeras Ave
Iron Ave
3rd
St
4th
St
Arn
o S
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11th
St
Fruit Ave
Coal Ave
Lomas Blvd
5th
St
Lead Ave
10th
St
Silver Ave
Mulb
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Slate Ave
Marquette Ave
Ed
ith B
lvd
Central Ave
Dr Martin Luther King Jr Ave
Tra
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Marble Ave
Inte
r sta
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5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH
47
SH
47
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
American
Linen
Springer PlazaOffice Complex
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NationsBank
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McDonald's (D2)PCE 0.5 UTCE 6.3cis-DCE 0.8trans-DCE 0.5 UVC 0.5 U
MNW-4 (D2)PCE 0.5 UTCE 3.1cis-DCE 3.4trans-DCE 0.7VC 0.5 U
MNW-5 (D2)PCE 0.9TCE 14.9cis-DCE 8.8trans-DCE 3.6VC 0.5 U
SFMW-23 (D2)PCE 0.5 UTCE 10.6cis-DCE 3.8trans-DCE 0.7VC 0.5 U
SFMW-44 (D2)
PCE 1.1TCE 14.3 =cis-DCE 7.6trans-DCE 3VC 0.5 U
SFMW-46 (D1/D2)PCE 0.5 UTCE 1.2
cis-DCE 1.2trans-DCE 0.5 UVC 0.5 U
D2E-P1 (D2)
PCE 0.5 UTCE 3.0cis-DCE 1.1trans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
10
5
I2/D1E-I1
D2E-I3
D2E-P1
0 300 600150 Feet
$Legend
@A Other Site Monitor Well
Presumed Source Area! Extraction Well
" Air Stripper Treatment Plant
! Injection Well
Railroad@A D2 Zone Monitor Well - Sample Aug. 2014
TCE concentration contour
(dashed where inferred)D2 Zone Monitoring Well – Not Sampled@A
Aquifer Zones:
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)
I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amsl
I2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amsl
D1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amsl
D2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amsl
D3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amsl
D4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
Volatile Organic Compounds:
Tetrachloroethene (PCE)
Trichloroethene (TCE)
Cis-1,2-dichloroethene (cis-DCE)
Trans-1,2-dichloroethene (trans-DCE)
Vinyl chloride (VC)
Units: micrograms per liter (μg/L)
Qualifers: J - estimated
U - not detected
JL - Estimated Concentration
= - detected concentration
NA – Not Analyzed
Date 2004 2005 2006 2007 2008 April 2009 Oct 2009 Feb 2010 Aug 2010 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE 1.2 = 1.4 = 0.85 = 0.8 JL 0.5 = 0.6 = 0.67 = 0.6 = 0.5 = 0.5 U 5.0 U 0.28 JJ 0.44 LJ 0.47 LJ 1 = 0.8 = 0.9
TCE 22 = 15 = 14 = 18.6 JL 15.1 = 13.1 = 13 = 11.1 = 10.5 = 8.6 = 19 = 9.1 = 14 = 12 = 16.4 = 15.4 = 14.9
cis-DCE 12 = 9.2 = 7.6 = 9.5 JL 9.8 = 7.4 = 8.2 = 7 = 7.2 = 5.3 = 12 = 5.5 = 8.2 = 8 = 8.6 = 9.5 = 8.8
trans-DCE 3.9 = 3.4 = 2.9 = 4.2 JL 3.9 = 3.3 = 3.4 = 3.2 = 2.5 = 1.7 = 4.7 LJ 2.3 = 2.8 = 3.1 = 3.6 = 4.2 = 3.6
VC 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW-5 (D2)
Date 2004 2005 2006 2007 2008 2009 Feb 2010 Aug 2010 Feb 2011 Aug-11 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE 1.3 = 1.2 = 0.5 U 1 JL 0.58 = 1.1 = 1.1 = 0.84 = 1.6 = 5.0 U 0.56 = 0.77 UM 0.62 = 0.6 = 0.8 = 1.1
TCE 12 = 13 = 7.3 = 13.9 JL 12 = 12 = 20.4 = 8.7 = 11.4 = 13 = 9.8 = 8.0 = 8.5 = 9.8 = 13.2 = 14.3 =
cis-DCE 7.2 = 6.7 = 4.7 = 7.5 JL 7.3 = 6.5 = 10.7 = 5.3 = 5.6 = 6.4 = 4.5 = 4.6 = 5.7 = 5.3 = 7.4 = 7.6
trans-DCE 2.2 = 3 = 2.3 = 3 JL 3.2 = 2.3 = 3.7 = 1.6 = 1.9 = 2.8 LJ 1.9 = 1.7 = 2.6 = 2.1 = 3.0 = 3
VC 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 = 0.5 =
SFMW-44 (D2)
Date 2008 2009 2010 2011 Oct-12 Nov-12 Dec-12 Jan-13 Feb-13 Mar-13 Aug 2013 Feb 2014 Aug 2014
PCE 0.5 U 0.5 U 0.5 U 5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
TCE 11 7.7 5.7 8.9 5 6.1 4.7 5.1 3.6 3.7 2.3 = 2.5 = 3.0
cis-DCE 4.6 3 2.3 3.3 1.7 2.1 1.8 2 1.4 1.4 0.9 = 1.0 = 1.1
trans-DCE 1.5 1 0.66 5 U 0.5 U 0.6 0.6 0.6 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
VC 0.5 U 0.5 U 0.5 U 5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
D2E-P1
Date 2003 2004 April 05 July 05 Feb 06 Aug 06 Feb 07 Oct 07 April 08 Oct 08 April 09 2010 2011 2012 2013 Feb 2014 Aug 2014
PCE 0.8 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
TCE 0.4 U 0.35 LJ 0.28 LJ 0.21 LJ 13 = 0.5 U 0.5 UJ 0.5 U 0.59 = 0.5 U 0.6 = 0.9 = 1.2 = 1.4 = 2.1 = 2.6 = 3.1
cis-DCE 0.3 U 0.5 U 0.5 U 0.5 U 4.9 = 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 = 0.96 UM 2.3 = 2.8 = 3.4
trans-DCE NA 0.5 U 0.5 U 0.5 U 1.3 = 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.19 LJ 0.37 LJ 0.6 = 0.7
VC 0.2 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW-4 (D2)
Date Feb 00 May 00 Feb 11 Aug 11 Feb 12 Aug 12 Feb 13 Aug 13 Feb 14 Aug 2014
PCE 1 U 1 U 0.5 U 5.0 U 0.5 U 0.041 LJ 0.26 LJ 0.5 U 0.5 U 0.5 U
TCE 1 U 1 = 0.74 = 11 = 8 = 11 = 10 9.2 = 6.6 = 6.3
cis-DCE 1 U 0.5 LJ 0.3 LJ 2.8 LJ 1.9 = 1.6 = 3.3 = 3 = 2.1 = 0.8
trans-DCE 1 U 1 U 0.5 U 1.1 LJ 0.82 = 0.80 = 2.3 = 2.2 = 1.2 = 0.5 U
VC 1 U 1 U 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
McDonalds (D2)
Notes:
1) TCE concentration contours based on analytical
results from August 25, 2014 sample event,
and historical data.
2) PDB – Passive diffusion bag depth interval
011464
R:\FRUITAVENUE_345406\MAPFILES\AUG_2014\FA_TCE_D3.MXD FLONDON 11/3/2014 5:11:01 PM
FIGURE 3-19
Distribution of Chlorinated Volatile Organic Compounds
in the D3 Aquifer Zone August 25 2014
Fruit Avenue Plume Superfund Site
Albuquerque, NM
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Sp
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Silver Ave
Copper Ave
Tijeras Ave
Do
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ipri
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Slate Ave
Silver Ave
Marquette Pl
Oak S
t
Syc
amor
eS
Map
le S
t
Sp
ruce S
t
Hig
h S
t
Gold Ave
Legion Rd
Tijeras Ave
Lu
na
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6t h
St
Medica
l Arts
Ave
Rid
ge P
l
Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Ke
leh
er
Ave
Sycam
ore
St
Spruce
St
7th
St
Ce
dar
St
Edith
Blv
d
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7th
St
ras Ave
Iron Ave
3rd
St
4th
St
Arn
o S
t
11th
St
Fruit Ave
Coal Ave
Lomas Blvd
5th
St
Lead Ave
Silver Ave
Mulb
err
y S
t
Slate Ave
Marquette Ave
Ed
ith B
lvd
Central Ave
Dr Martin Luther King Jr Ave
Tra
nquil i
no C
t
Marble Ave
Inte
r sta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH
47
SH
47
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
American
Linen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
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MNW-5 (D3)PCE 0.5 UTCE 16.4cis-DCE 9.9trans-DCE 6.1VC 0.5 U
SFMW-35 (D3)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-41 (D3/D4)PCE 0.5 UTCE 0.6cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
5
10
I2/D1E-I1
D2E-I3
D2E-P1
0 300 600150 Feet
$Legend
@A Other Site Monitor Well
Presumed Source Area! Extraction Well
" Air Stripper Treatment Plant
! Injection Well
Railroad@A D3 Zone Monitor Well - Sample Aug. 2014
TCE concentration contour
(dashed where inferred)D3 Zone Monitoring Well – Not Sampled@A
Aquifer Zones:
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)
I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amsl
I2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amsl
D1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amsl
D2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amsl
D3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amsl
D4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
Volatile Organic Compounds:
Tetrachloroethene (PCE)
Trichloroethene (TCE)
Cis-1,2-dichloroethene (cis-DCE)
Trans-1,2-dichloroethene (trans-DCE)
Vinyl chloride (VC)
Units: micrograms per liter (μg/L)
Qualifers: J - estimated
U - Not Detected
UJ - Not Detected,
estimated concentration
JL - Estimated Concentration
= - detected concentration
NA – Not Analyzed
Date 2004 2005 2006 2007 2008 April 2009 Oct 2009 Feb 2010 Aug 2010 Feb 2011 Aug-11 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE 0.68 = 1.3 = 0.89 = 0.9 = 0.8 = 0.5 J 0.41 LJ 0.5 U 0.5 U 0.5 U 5.0 U 0.42 LJ 0.74 = 0.74 = 0.9 = 0.5 U 0.5 U
TCE 10 = 13 = 16 = 19.6 = 19.2 = 17.8 J 16 = 15.8 = 17.3 = 18.2 = 27 = 15 = 22 = 16 = 19 = 16.1 = 16.4
cis-DCE 4.9 = 6.7 = 8.3 = 10.8 = 9.4 = 9.1 J 9.4 = 10.6 = 9.5 = 8.8 = 13 = 6.9 = 10 = 8.7 = 8.2 = 9 = 9.9
trans-DCE 1.1 = 1.7 = 2.1 = 3.9 = 3.5 = 3.7 J 4.2 = 15.8 = 4.2 = 2.9 = 4.9 LJ 2.6 = 3.0 = 3.3 = 3.8 = 4.8 = 6.1
VC 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 2.0 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW-5 (D3)
Notes:
1) TCE concentration contours based on analytical
results from August 25, 2014 sample event,
and historical data.
2) PDB – Passive diffusion bag depth interval
011465
R:\FRUITAVENUE_345406\MAPFILES\AUG_2014\FA_TCE_D4.MXD FLONDON 11/3/2014 4:40:37 PM
FIGURE 3-20
Distribution of Chlorinated Volatile Organic Compounds
in the D4 Aquifer Zone August 25 2014
Fruit Avenue Plume Superfund Site
Albuquerque, NM
"
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!
!!
Sp
ruce S
t
Silver Ave
Copper Ave
Tijeras Ave
Do
n C
ipri
an
oC
t
Slate Ave
Silver Ave
Marquette Pl
Oak S
t
Syc
amor
e
Map
le S
t
Sp
ruce S
t
Hig
h S
t
Gold Ave
gion Rd
Tijeras Ave
Lu
na
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6t h
St
Med
ical Arts
Ave
Rid
ge P
l
Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Ke
leh
er
Ave
Sycam
ore
St
Spruce
St
7th
St
Ce
da
r S
t
Edith
Blv
d
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7th
St
eras Ave
Iron Ave
3rd
St
4th
St
Arn
o S
t
11th
St
Fruit Ave
Coal Ave
Lomas Blvd
5th
St
Lead Ave
Silver Ave
Mulb
err
y S
t
Slate Ave
Marquette Ave
Ed
ith B
lvd
Central Ave
Dr Martin Luther King Jr Ave
Tra
nquil i
no C
t
Marble Ave
Inte
r sta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH
47
SH
47
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
American
Linen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank @A
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SFMW-41 (D3/D4)
PCE 0.5 UTCE 0.6cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
I2/D1E-I1
D2E-I3
D2E-P1
0 300 600150 Feet
$Legend
@A Other Site Monitor Well
Presumed Source Area! Extraction Well
" Air Stripper Treatment Plant
! Injection Well
Railroad@A D4 Zone Monitor Well - Sample Aug. 2014
TCE concentration contour
(dashed where inferred)D4 Zone Monitoring Well – Not Sampled@A
Aquifer Zones:
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)
I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amsl
I2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amsl
D1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amsl
D2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amsl
D3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amsl
D4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
Volatile Organic Compounds:
Tetrachloroethene (PCE)
Trichloroethene (TCE)
Cis-1,2-dichloroethene (cis-DCE)
Trans-1,2-dichloroethene (trans-DCE)
Vinyl chloride (VC)
Units: micrograms per liter (μg/L)
Qualifers: J - estimated
U - Not Detected
UJ - Not Detected,
estimated concentration
JL - Estimated Concentration
= - detected concentration
NA – Not Analyzed
Date 2004 2005 2007 April 2009 Oct 2009 Feb 2010 Aug 2010 Feb 2011 Aug 2011 Feb 2012 Aug 2012 Feb 2013 Aug 2013 Feb 2014 Aug 2014
PCE 0.5 U 0.5 U 0.5 U 0.5 UJ 1 = 0.5 U 0.54 = 0.5 U 0.5 U 0.3 LJ 0.32 LJ 0.27 LJ 0.5 U 0.5 U 0.5 U
TCE 0.28 = 0.52 = 1.3 = 0.5 UJ 1.6 = 1.2 LJ 1 = 0.6 = 1.1 LJ 0.31 LJ 0.75 = 0.36 LJ 0.8 = 0.5 U 0.6
cis-DCE 0.5 U 0.5 U 0.5 U 0.5 UJ 0.72 = 0.5 U 0.39 LJ 0.5 U 0.5 U 0.5 U 0.17 LJ 0.5 U 0.5 U 0.5 U 0.5 U
trans-DCE 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
VC 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
SFMW-41 (D3/D4)
Notes:
1) TCE concentration contours based on analytical
results from August 25, 2014 sample event,
and historical data.
2) PDB – Passive diffusion bag depth interval
011466
0
10
20
30
40
50
60
70
1995 1998 2001 2004 2006 2009 2012 2014 2017
TCE
Conc
entr
aon
(μg/
L)SFMW-20 (I1)
SFMW-25 (I1)
SFMW-47 (I1)
ES110514201639SPB
FIGURE 3-21I1 Aquifer Zone - TCE Concentra on Trends over Time, November 1997 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
011467
ES110514201639SPB
FIGURE 3-22I2 Aquifer Zone - TCE Concentra on Trends over Time, April 1997 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
0
20
40
60
80
100
120
1995 1998 2001 2004 2006 2009 2012 2014 2017
TCE
Conc
entr
aon
(μg/
L)
HSM-I2-5 (I2)
MNW-14 (I2) *
SFMW-17 (I2)
SFMW-19(I2)
SFMW-21 (I2)
SFMW-26 (I2)
SFMW-32 (I2)
SFMW-47 (I2)
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ES110514201639SPB
FIGURE 3-23D1 Aquifer Zone - TCE Concentra on Trends over Time, October 1997 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
0
2
4
6
8
10
12
14
16
18
20
1995 1998 2001 2004 2006 2009 2012 2014 2017
TCE
Conc
entr
aon
(μg/
L)MNW-13 (D1)
MNW-15 (D1)
MNW-4 (D1)
MNW-5 (D1)
SFMW-22 (D1)
SFMW-38 (D1)
SFMW-46 (D1)
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ES110514201639SPB
FIGURE 3-24D2 Aquifer Zone - TCE Concentra on Trends over Time, November 1997 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
0
5
10
15
20
25
30
35
40
45
1995 1998 2001 2004 2006 2009 2012 2014 2017
TCE
Conc
entr
aon
(μg/
L)MNW-15 (D2)
MNW-5 (D2)
MNW-4(D2)
SFMW-23 (D2)
SFMW-39 (D2)
SFMW-44 (D2)
SFMW-45 (D2)
SFMW-46 (D2)
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ES110514201639SPB
FIGURE 3-25D3 Aquifer Zone - TCE Concentra on Trends over Time, July 1998 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
0
5
10
15
20
25
30
1995 1998 2001 2004 2006 2009 2012 2014 2017
TCE
Conc
entr
aon
(μg/
L)
MNW-15 (D3)
MNW-5 (D3)
SFMW-35 (D3)
SFMW-40 (D3)
SFMW-41 (D3/D4)
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ES110514201639SPB
FIGURE 3-26Upgradient Offsite Plume - 12 and D1 Aquifer Zones - TCE Concentra on Trends over Time, April 2005 through August 2014Fruit Avenue Plume Superfunds Site, Albuquerque, NM
0
5
10
15
20
25
30
35
40
45
50
1995 1998 2001 2004 2006 2009 2012 2014 2017
TCE
Conc
ente
raon
(μg/
L)
MNW-1 (I2)
MNW-9 (I2)
MNW-11 (I2)
MNW-9 (D1)
MNW-11 (D1)
MNW-12 (D1)
SFMW-14(D1)
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2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015
Co
nta
min
an
t C
on
ce
ntr
atio
n (
µg/L
)
0
2
4
6
8
10
12
14
16
EPA MCL for TCE
Run RestMode Mode
FIGURE 3-27
TCE Concentration in Untreated Influent Groundwater
January 2005 through August 2014
Fruit Avenue Plume Superfund Site, Albuquerque, NM
CONTINUOUS
OPERATIONS
PULSED OPERATIONS
Run RestMode Mode
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Appendix A Fruit Avenue Plume Superfund Site Summary of
the First Semiannual Groundwater Sampling Event for 2014
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APPENDIX A: FRUIT AVENUE PLUME SUPERFUND SITE SUMMARY OF THE FIRST SEMIANNUAL GROUNDWATER SAMPLING EVENT FOR 2014
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TRANSMITTAL OF DOCUMENTS FOR ACCEPTANCE BY EPA DATE:
06/27/2014
TRANSMITTAL NO. ES050514041759SPB DCN: 0003‐02108
TO: Bartolomé Cañellas, Remedial Project Manager U.S. EPA Region 6 1445 Ross Avenue 12th Floor Dallas, TX 75202
FROM: Brian Wied, Project Manager CH2M HILL/DFW 12750 Merit Drive Suite 1100 Dallas, TX 75251
X New Transmittal
Resubmittal of Transmittal No. _________
SUBTASK NO.
DELIVERABLE NO. OF COPIES REMARKS
345406.PJ.09 Final Summary of the First Semiannual Groundwater Sampling Event for 2014: Fruit Avenue Plume Superfund Site
Electronic File via SharePoint Site Groundwater Monitoring Reports
Bartolomé Cañellas /EPA Remedial Project Manager U.S. EPA Region 6 (6SF‐LP) 1455 Ross Avenue, 12th Floor Dallas, TX 75202
345406.PJ.09
Final Summary of the First Semiannual Groundwater Sampling Event for 2014: Fruit Avenue Plume Superfund Site
Electronic File via SharePoint Site Groundwater Monitoring Reports
Sabino Rivera/NMED 1190 St. Francis Dr. #N2300 Santa Fe, NM 87502 (505) 827‐0387
345406.PJ.09
Final Summary of the First Semiannual Groundwater Sampling Event for 2014: Fruit Avenue Plume Superfund Site
Electronic File via SharePoint Site Groundwater Monitoring Reports
Billy Gallegos/CoA 1 Civic Plaza Suite 3023 Albuquerque, NM 87103 (505) 768‐2669
345406.PJ.09
Final Summary of the First Semiannual Groundwater Sampling Event for 2014: Fruit Avenue Plume Superfund Site
Electronic File via SharePoint Site Groundwater Monitoring Reports
Rick Shean/Water Quality Hydrologist Albuquerque Bernalillo County Water Utility Authority P.O. Box 1293 Albuquerque, NM 87103 (505) 768‐3634
ACCEPTANCE ACTION DOCUMENTS FOUND ACCEPTABLE (LIST BY SUBTASK NO.)
NAME/TITLE/SIGNATURE OF REVIEWER
DATE
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CH2M HILL 12750 Merit Drive Suite 1100 Dallas, TX 75251 Tel 972.663-2291 Fax 972.385-5113
ES050514041759SPB
345406.PJ.09 June 27, 2014 Bartolomé Cañellas Remedial Project Manager U.S. EPA Region 6, 6SF‐LP 1445 Ross Avenue 12th Floor Dallas, TX 75202 Subject: Contract No. EP‐W‐06‐021
Task Order No. 0003‐RALR‐06DD Fruit Avenue Plume Superfund Site Final Summary of the First Semiannual Groundwater Sampling Event for 2014
Dear Mr. Cañellas:
CH2M HILL is pleased to provide you with one electronic copy of the final Summary of the First Semiannual Groundwater Sampling Event for 2014: Fruit Avenue Plume Superfund Site, via the following SharePoint site link:
Groundwater Monitoring Reports Link
If you have any questions regarding this document, feel free to contact me at (972) 663‐2291.
Sincerely,
CH2M HILL
Brian Wied, P.G. Project Manager
REF DCN ‐ 0003‐02108
cc: Peter van Noort/CH2M HILL Bill LeFevre/CH2M HILL
File
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FAP_2014_LTM_SEMI 1 ES050514041759SPB
T E C H N I C A L M E M O R A N D U M — F I N A L Fruit Avenue Plume Superfund Site Long-term Remedial Action Summary of the First Semiannual Groundwater Sampling Event for 2014 PREPARED FOR: Bartolomé Cañellas /EPA Region 6 Remedial Project Manager
PREPARED BY: CH2M HILL
DATE
COPY TO:
June 27, 2014
Sabino Rivera/NMED Billy Gallegos/AEHD Rick Shean/ABCWUA
PROJECT: EPA Region 6 Response Action Contract No. EP‐W‐06‐021 Task Order No. 0003‐RALR‐06DD CH2M HILL Project No. 345406.PJ.09
DCN: 0003‐02108
Introduction This technical memorandum (TM) summarizes field sampling activities and presents the laboratory analysis results for the first semiannual groundwater sampling event conducted in 2014 at the Fruit Avenue Plume Superfund Site (site) located in downtown Albuquerque, New Mexico. Field activities included water level measurements at accessible site monitor wells and collection of groundwater samples from designated monitor wells. A comprehensive and detailed evaluation of the data presented in this TM will be provided in the 2014 annual groundwater sampling report.
Semiannual groundwater monitoring is being conducted to obtain information for assessing the effectiveness of the groundwater long‐term remedial action (LTRA) that has been underway at the site since 2005. Groundwater sampling activities were performed in accordance with the U.S. Environmental Protection Agency (EPA)–approved sampling and analysis plan, which consists of the field sampling plan (Version 2.1) and the quality assurance project plan (Version 3.0), (CH2M HILL 2010a, 2007). As outlined in the field sampling plan, 45 long‐term monitoring (LTM) wells were sampled during the event. Water level measurements were collected at 103 monitoring well locations.
The contaminants of concern and their corresponding remediation goals for groundwater at the site include the following chlorinated volatile organic compounds (CVOC): tetrachloroethene (PCE)—5 micrograms per liter (µg/L); trichloroethene (TCE)—5 µg/L; cis‐1,2‐dichloroethene (DCE)—70 µg/L; and trans‐1,2‐DCE—100 µg/L. Vinyl chloride (VC) was not identified as a contaminant of concern in the Record of Decision (EPA 2001), but is routinely monitored because it is a TCE breakdown product.
Description of Field Activities A team composed of three CH2M HILL representatives and two New Mexico Environment Department (NMED) personnel performed the sampling event. Field activities were conducted from February 16 through 18, 2014. Monitor well locations are shown on the site map (Figure 1).
Water Level Measurement Activities On February 16, 2014, prior to groundwater sampling, water levels were measured at 103 of the 104 site monitor wells. Monitor well SPSC‐W13, a shallow aquifer zone well installed as part of an unrelated underground storage
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tank investigation has been paved over and is no longer accessible. The air stripper treatment plant has been shut down since May 20, 2013; therefore, water level measurements from monitoring wells located near the groundwater extraction and injection wells are expected to show the effects of a recovering water table. The water level measurements and corresponding aquifer zone for each monitor well are provided in Table 1.
Groundwater Sampling Activities In preparation for the February 2014 groundwater sampling event, passive diffusion bags (PDBs) that are sampled as part of the LTM program were replaced. The PDB replacement was done to guard against unnoticed biofouling and to prevent inadvertent sampling of the wrong PDB. PDBs that are not part of the LTM program were removed and their associated weights and tethers stored in the monitor wells for future use. The PDBs were replaced on January 26, 2014, which allowed more than the manufacturer-recommended 2 weeks for organic-free water placed in the PDBs to equilibrate with the groundwater.
Groundwater sampling was conducted on February 17 and 18, 2014. The sample collection process generally consists of sampling a single PDB that was previously determined to be representative of the screen interval in the sampled monitor well. The number of PDBs and their depth of installation are dependent upon the length and depth of the monitor well screen interval. During this sampling event, only a subset of the total number of PDBs deployed at the site was sampled, based on recommendations provided in the Long-term Monitoring Optimization Report (CH2M HILL 2009) and Field Sampling Plan Version 2.1 Addendum 1 (CH2M HILL 2010b). The targeting of specific depth intervals for PDB sampling was based on trends in contaminant stratification observed along the well screen interval during previous sampling events. Based on previous trends, the PDB or PDBs with the historical maximum detected CVOC concentrations were sampled. If all previous PDB samples at a given well location previously indicated nondetect values, then a single PDB located approximately mid-screen was selected as being representative and sampled.
The following wells were added to LTM program as recommended in the Long-term Monitoring Optimization Report (CH2M HILL 2009) and the well abandonment TM (CH2M HILL 2010c): McDonalds (D2) and SFMW-28 (I2). Prior to the sampling event, the optimal depth for PDB sampling in these two wells, had not yet been determined. Therefore, all PDBs were sampled to evaluate vertical TCE concentration stratification in the wells. The optimal sampling depth at these locations is evaluated in this TM, and a recommendation for future sampling at these two locations is provided.
While sampling at each location, the PDBs were removed from the well and placed on plastic sheeting to prevent contact with the ground. A CVOC sample was collected by pouring water from the PDB directly into the sample containers. After sample collection, each PDB was visually inspected for physical wear and biofilm, and if it held water, it was reused. Those PDBs that were sampled were refilled with Type II organic-free water and lowered back into the well in preparation for the next groundwater sampling event. Each of the PDBs sampled have been in place since they were replaced on January 26, 2014.
Groundwater samples were collected from 58 PDBs at 45 LTM wells. Eleven field quality control samples were also collected. Samples were shipped on the date of sample collection to the EPA Environmental Services Branch Region 6 Laboratory for low-level VOCs analysis using Contract Laboratory Program Method OLM04.2.
Groundwater Sampling Results Groundwater elevations for each aquifer zone are presented in Table 1 and groundwater elevation contours are illustrated on Figures 2 through 8. Concentrations for the contaminants of concern detected in each aquifer zone during the February 2014 event, as well as previous sampling events, are presented in Table 2 and the distribution of TCE in groundwater is illustrated on Figures 9 through 15.
Recommendations The historical TCE concentrations for each of the PDBs sampled at monitoring wells new to the LTM program are reported in Table 3 and illustrated on Figures 16 and 17. At the McDonalds (D2) and SFMW-28 (I2) monitoring wells a single PDB has been selected as representative of the screen interval. For future groundwater monitoring events, sampling of the following PDBs is recommended:
FAP_2014_LTM_SEMI 2 ES050514041759SPB
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FRUIT AVENUE PLUME SUPERFUND SITE LONG-TERM REMEDIAL ACTION SUMMARY OF THE FIRST SEMIANNUAL GROUNDWATER SAMPLING EVENT FOR 2014
• The 8-foot PDB will be sampled at McDonalds (D2), because more than half of the TCE exceedances are from this interval.
• The 5-foot PDB will be sampled at SFMW-28 (I2), because it has produced one of the two TCE detections in the well, and because it is in the middle of the screen interval.
Works Cited CH2M HILL. 2007. Quality Assurance Project Plan, Version 3.0, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. June.
CH2M HILL. 2009. Long-term Monitoring Optimization Report, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. September.
CH2M HILL. 2010a. Field Sampling Plan Version 2.1, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. March.
CH2M HILL. 2010b. Field Sampling Plan Version 2.1, Addendum 1, Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico. December.
CH2M HILL. 2010c. Fruit Avenue Plume Superfund Site – Monitor Well Abandonment Rationale. December.
U.S. Environmental Protection Agency (EPA). 2001. Record of Decision, Fruit Avenue Plume Site, Albuquerque, New Mexico. CERCLIS # NMD986668911. September.
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Tables
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TABLES
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TABLE 1Water Level Measurements—February 16, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monitor Well IDAquifer Zone Designation*
TOC Elevation (feet amsl)
Depth to Water (feet BTOC)
Water Level Elevation (feet amsl)
Date
DM‐01 S 4,954.80 32.87 4,921.93 16‐Feb‐14
DM‐05 S 4,954.92 33.61 4,921.31 16‐Feb‐14
DM‐06 I1/I2 4,953.60 37.05 4,916.55 16‐Feb‐14
DM‐07 I1/I2 4,954.35 37.23 4,917.12 16‐Feb‐14
DM‐08 I1/I2 4,954.85 37.52 4,917.33 16‐Feb‐14
DM‐09 S 4,954.83 36.32 4,918.51 16‐Feb‐14
DM‐10 S 4,954.24 36.69 4,917.55 16‐Feb‐14
DM‐11 S 4,954.15 29.21 4,924.94 16‐Feb‐14
DM‐12 I1/I2 4,953.79 27.84 4,925.95 16‐Feb‐14
DM‐13 (S) S 4,954.11 33.04 4,921.07 16‐Feb‐14
DM‐13 (I1) I1 4,954.11 32.28 4,921.83 16‐Feb‐14
DM‐13 (I2) D1 4,954.09 31.32 4,922.77 16‐Feb‐14
DM‐13 (D1) D2 4,954.08 28.53 4,925.55 16‐Feb‐14
HSM‐I2‐4 I2 4,957.10 31.52 4,925.58 16‐Feb‐14
HSM‐I2‐5 I2 4,957.10 33.06 4,924.04 16‐Feb‐14
McDonald's D2 4,959.00 44.65 4,914.35 16‐Feb‐14
MNW‐1 (I2) I2 4,955.20 25.52 4,929.68 16‐Feb‐14
MNW‐10 (I1) I1 4,957.30 28.82 4,928.48 16‐Feb‐14
MNW‐10 (I2) I2 4,957.30 28.79 4,928.51 16‐Feb‐14
MNW‐11 (I1) I1 4,954.64 21.03 4,933.61 16‐Feb‐14
MNW‐11 (I2) I2 4,954.67 21.05 4,933.62 16‐Feb‐14
MNW‐11 (D1) D1 4,954.47 20.88 4,933.59 16‐Feb‐14
MNW‐11 (D2) D2 4,954.66 21.09 4,933.57 16‐Feb‐14
MNW‐12 (I1) I1 4,954.34 20.67 4,933.67 16‐Feb‐14
MNW‐12 (I2) I2 4,954.37 20.73 4,933.64 16‐Feb‐14
MNW‐12 (D1) D1 4,954.32 20.64 4,933.68 16‐Feb‐14
MNW‐12 (D2) D2 4,954.36 20.72 4,933.64 16‐Feb‐14
MNW‐13 (D1) D1 5,071.72 164.42 4,907.30 16‐Feb‐14
MNW‐13 (D2) D2 5,071.76 164.21 4,907.55 16‐Feb‐14
MNW‐13 (D3) D3 5,071.64 163.61 4,908.03 16‐Feb‐14
FAP_2014_LTM_SEMI_TABLE 1ES050514041759SPB PAGE 1 OF 4
011485
TABLE 1Water Level Measurements—February 16, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monitor Well IDAquifer Zone Designation*
TOC Elevation (feet amsl)
Depth to Water (feet BTOC)
Water Level Elevation (feet amsl)
Date
MNW‐13 (D4) D4 5,071.71 163.20 4,908.51 16‐Feb‐14
MNW‐14 (I2) I2 4,955.64 28.89 4,926.75 16‐Feb‐14
MNW‐14 (D1) D1 4,955.64 27.16 4,928.48 16‐Feb‐14
MNW‐14 (D2) D2 4,955.63 26.75 4,928.88 16‐Feb‐14
MNW‐15 (D1) D1 5,123.53 230.99 4,892.54 16‐Feb‐14
MNW‐15 (D2) D2 5,123.52 219.24 4,904.28 16‐Feb‐14
MNW‐15 (D3) D3 5,123.45 218.93 4,904.52 16‐Feb‐14
MNW‐16 (D1) D1 5,065.93 158.49 4,907.44 16‐Feb‐14
MNW‐16 (D2) D2 5,065.95 158.04 4,907.91 16‐Feb‐14
MNW‐16 (D3) D3 5,065.92 157.76 4,908.16 16‐Feb‐14
MNW‐16 (D4) D4 5,066.00 157.45 4,908.55 16‐Feb‐14
MNW‐2 (I2) I2 4,956.10 31.08 4,925.02 16‐Feb‐14
MNW‐3 (D1) D1 4,972.50 57.80 4,914.70 16‐Feb‐14
MNW‐3 (D2) D2 4,972.50 58.65 4,913.85 16‐Feb‐14
MNW‐3 (D3) D3 4,972.50 59.39 4,913.11 16‐Feb‐14
MNW‐4 (D1) D1 5,061.40 154.40 4,907.00 16‐Feb‐14
MNW‐4 (D2) D2 5,061.40 154.46 4,906.94 16‐Feb‐14
MNW‐4 (D3) D3 5,061.40 154.06 4,907.34 16‐Feb‐14
MNW‐5 (D1) D1 4,993.60 83.25 4,910.35 16‐Feb‐14
MNW‐5 (D2) D2 4,993.60 82.95 4,910.65 16‐Feb‐14
MNW‐5 (D3) D3 4,993.60 82.45 4,911.15 16‐Feb‐14
MNW‐5 (D4) D4 4,992.51 81.47 4,911.04 16‐Feb‐14
MNW‐6 (D1) D1 4,967.90 55.74 4,912.16 16‐Feb‐14
MNW‐6 (D2) D2 4,967.90 55.60 4,912.30 16‐Feb‐14
MNW‐6 (D3) D3 4,967.90 55.45 4,912.45 16‐Feb‐14
MNW‐7 (D4) D4 5,012.30 101.53 4,910.77 16‐Feb‐14
MNW‐8 (I1) I1 4,954.60 24.49 4,930.11 16‐Feb‐14
MNW‐8 (I2) I2 4,954.70 24.43 4,930.27 16‐Feb‐14
MNW‐9 (I1) I1 4,954.60 23.01 4,931.59 16‐Feb‐14
MNW‐9 (I2) I2 4,954.60 22.95 4,931.65 16‐Feb‐14
FAP_2014_LTM_SEMI_TABLE 1ES050514041759SPB PAGE 2 OF 4
011486
TABLE 1Water Level Measurements—February 16, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monitor Well IDAquifer Zone Designation*
TOC Elevation (feet amsl)
Depth to Water (feet BTOC)
Water Level Elevation (feet amsl)
Date
MNW‐9 (D1) D1 4,954.37 22.82 4,931.55 16‐Feb‐14
MNW‐9 (D2) D2 4,954.36 22.65 4,931.71 16‐Feb‐14
SFMW‐01 S 4,954.29 31.52 4,922.77 16‐Feb‐14
SFMW‐03 S 4,953.99 32.76 4,921.23 16‐Feb‐14
SFMW‐07 S 4,953.48 30.13 4,923.35 16‐Feb‐14
SFMW‐10 I2 4,953.85 28.28 4,925.57 16‐Feb‐14
SFMW‐11 S 4,954.83 27.94 4,926.89 16‐Feb‐14
SFMW‐12 I1 4,954.69 27.76 4,926.93 16‐Feb‐14
SFMW‐13 I2 4,954.59 27.61 4,926.98 16‐Feb‐14
SFMW‐14 D1 4,953.77 26.60 4,927.17 16‐Feb‐14
SFMW‐15 S 4,954.31 34.47 4,919.84 16‐Feb‐14
SFMW‐16 I1 4,954.53 33.91 4,920.62 16‐Feb‐14
SFMW‐17 I2 4,954.55 32.52 4,922.03 16‐Feb‐14
SFMW‐18 I1 4,952.96 29.17 4,923.79 16‐Feb‐14
SFMW‐20 I1 4,954.96 43.65 4,911.31 16‐Feb‐14
SFMW‐21 I2 4,954.76 43.26 4,911.50 16‐Feb‐14
SFMW‐22 D1 4,954.80 42.41 4,912.39 16‐Feb‐14
SFMW‐23 D2 4,954.86 42.62 4,912.24 16‐Feb‐14
SFMW‐24 S 4,952.65 33.33 4,919.32 16‐Feb‐14
SFMW‐25 I1/I2 4,952.75 34.41 4,918.34 16‐Feb‐14
SFMW‐26 I2 4,952.69 34.71 4,917.98 16‐Feb‐14
SFMW‐27 I2 4,953.70 27.54 4,926.16 16‐Feb‐14
SFMW‐28 I2 4,952.24 28.44 4,923.80 16‐Feb‐14
SFMW‐31 I2 4,955.46 51.90 4,903.56 16‐Feb‐14
SFMW‐32 I2 4,963.63 58.98 4,904.65 16‐Feb‐14
SFMW‐33 D2 4,954.06 39.19 4,914.87 16‐Feb‐14
SFMW‐34 D4 4,954.04 42.61 4,911.43 16‐Feb‐14
SFMW‐35 D3 4,954.64 43.34 4,911.30 16‐Feb‐14
SFMW‐36 D4 4,954.64 44.06 4,910.58 16‐Feb‐14
SFMW‐37 I2 4,953.36 39.00 4,914.36 16‐Feb‐14
FAP_2014_LTM_SEMI_TABLE 1ES050514041759SPB PAGE 3 OF 4
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TABLE 1Water Level Measurements—February 16, 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
Monitor Well IDAquifer Zone Designation*
TOC Elevation (feet amsl)
Depth to Water (feet BTOC)
Water Level Elevation (feet amsl)
Date
SFMW‐38 D1 4,963.92 55.59 4,908.33 16‐Feb‐14
SFMW‐39 D2 4,962.40 54.10 4,908.30 16‐Feb‐14
SFMW‐40 D3 4,963.18 55.31 4,907.87 16‐Feb‐14
SFMW‐41 D3 4,963.14 55.66 4,907.48 16‐Feb‐14
SFMW‐43 I1 4,967.52 64.39 4,903.13 16‐Feb‐14
SFMW‐44 D2 4,967.57 57.48 4,910.09 16‐Feb‐14
SFMW‐45 D2 5,001.06 91.92 4,909.14 16‐Feb‐14
SFMW‐46 D1/D2 5,026.05 119.38 4,906.67 16‐Feb‐14
SFMW‐47 I1/I2 4,954.11 32.48 4,921.63 16‐Feb‐14
SPSC‐MW19 S 4,954.77 40.01 4,914.76 16‐Feb‐14
SPSC‐MW5 S 4,956.61 39.11 4,917.50 16‐Feb‐14
WB‐01 (I) I1/I2 4,954.05 26.43 4,927.62 16‐Feb‐14
WB‐02 (I) I1/I2 4,954.05 25.29 4,928.76 16‐Feb‐14
Notes:
amsl = above mean sea levelBTOC = below top of casingID = IdentificationTOC = top of casingD1 = Deep Zone 1D2 = Deep Zone 2D3 = Deep Zone 3D4 = Deep Zone 4I1 = Intermediate Zone 1I2 = Intermediate Zone 2S = Shallow Zone
* ‐ See sampling and analysis plan for discussion of site hydrogeology and aquifer zone designations.
FAP_2014_LTM_SEMI_TABLE 1ES050514041759SPB PAGE 4 OF 4
011488
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2b
AML (Elite) supply unknown FR844 NA 5/13/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FR846 NA 5/13/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FW851 NA 9/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FW852 NA 9/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UAML (Elite) supply unknown FW853 NA 9/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
Atomic‐MW1 unknown NA 5/10/2020 0:00 unknownAtomic‐MW1 unknown FEF87 NA 8/12/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
COKE Supply unknown NA 5/10/2020 0:00 unknownCOKE Supply unknown FAR03 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 1 = 10 = 1 UCOKE Supply unknown FAR01 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 1 = 11 = 1 UCOKE Supply unknown FAR02 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 1 = 11 = 1 UCOKE Supply unknown FAR04 NA 8/23/1999 0:00 unknown GW µg/L 4 = 1 U 2 = 11 = 1 UCOKE Supply unknown FAQ98 NA 8/23/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 12 = 1 UCOKE Supply unknown FAQ99 NA 8/23/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 13 = 1 UCOKE Supply unknown FAR00 NA 8/23/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 13 = 1 UCOKE Supply unknown FW818 NA 8/11/1997 0:00 unknown GW µg/L 1 = 1 U 1 U 1 = 1 UCOKE Supply unknown FW817 NA 8/11/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UCOKE Supply unknown FW821 NA 8/11/1997 0:00 unknown GW µg/L 3 = 1 U 1 = 5 = 1 UCOKE Supply unknown FW820 NA 8/11/1997 0:00 unknown GW µg/L 4 = 1 U 1 = 11 = 1 UCOKE Supply unknown FW819 NA 8/11/1997 0:00 unknown GW µg/L 4 = 1 U 2 = 11 = 1 UCOKE Supply unknown FW815 NA 8/11/1997 0:00 unknown GW µg/L 5 U 5 U 5 U 5 U 5 UCOKE Supply unknown FW816 NA 8/11/1997 0:00 unknown GW µg/L 5 U 5 U 5 U 5 U 5 UCOKE Supply unknown not assigned‐21 NA 7/7/1989 0:00 unknown GW µg/L 2.4 = T 1.2 = 13.1 =COKE Supply unknown not assigned‐4 NA 7/7/1989 0:00 unknown GW µg/L 2.4 = T 1.2 = 13.1 =COKE Supply unknown not assigned‐20 NA 4/25/1989 0:00 unknown GW µg/L 7 = 14.5 =COKE Supply unknown not assigned‐3 NA 4/25/1989 0:00 unknown GW µg/L 7 = ND ND 14.5 =COKE Supply unknown not assigned‐2 NA 8/20/1987 0:00 unknown GW µg/L ND ND ND NDCOKE Supply unknown not assigned‐18 NA 12/3/1986 0:00 unknown GW µg/L TCOKE Supply unknown not assigned‐1 NA 12/3/1986 0:00 unknown GW µg/L ND T ND ND
Conv. Center unknown NA 5/10/2020 0:00 unknownConv. Center unknown not assigned‐36 NA 1/18/1989 0:00 unknown GW µg/L 14 = 4 = 2.6 =Conv. Center unknown not assigned‐14 NA 1/18/1989 0:00 unknown GW µg/L 14 = ND 4 = 2.6 =Conv. Center unknown not assigned‐35 NA 4/28/1988 0:00 unknown GW µg/L 25 = 14 = 4 =Conv. Center unknown not assigned‐13 NA 4/28/1988 0:00 unknown GW µg/L 25 = ND 14 = 4 =Conv. Center unknown not assigned‐34 NA 2/12/1988 0:00 unknown GW µg/L 30 = 22 = 2 =Conv. Center unknown not assigned‐12 NA 2/12/1988 0:00 unknown GW µg/L 30 = ND 22 = 2 =
D2E‐P1 (D2) NA 5/10/2020 0:00 unknownD2E‐P1 (D2) D2 FAP SP‐1 NA 8/14/13 Grab GW µg/L 0.9 0.5 U 0.5 U 2.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 8/14/13 Grab GW µg/L 0.8 0.5 U 0.5 U 2.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 7/15/13 Grab GW µg/L 1.2 0.5 U 0.5 U 3.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 7/15/13 Grab GW µg/L 1.2 0.5 U 0.5 U 2.8 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 6/10/13 Grab GW µg/L 1.3 0.5 U 0.5 U 3.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 6/10/13 Grab GW µg/L 1.2 0.5 U 0.5 U 3.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 5/20/13 Grab GW µg/L 1.6 0.5 U 0.5 U 4.5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 5/20/13 Grab GW µg/L 1.7 0.5 U 0.5 U 4.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 4/16/13 Grab GW µg/L 1.3 0.5 U 0.5 U 3.5 0.5 U
Matrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling Method
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 1 OF 64
011489
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 4/16/13 Grab GW µg/L 1.2 0.5 U 0.5 U 3.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 3/18/13 Grab GW µg/L 1.4 0.5 U 0.5 U 3.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 3/18/13 Grab GW µg/L 1.4 0.5 U 0.5 U 3.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 2/20/13 Grab GW µg/L 1.4 0.5 U 0.5 U 3.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 2/20/13 Grab GW µg/L 1.4 0.5 U 0.5 U 3.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 1/21/13 Grab GW µg/L 2 0.5 U 0.6 5.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 1/21/13 Grab GW µg/L 1.9 0.5 U 0.6 4.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 12/19/12 Grab GW µg/L 1.8 0.5 U 0.6 4.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 12/19/12 Grab GW µg/L 1.7 0.5 U 0.5 4.5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 11/19/12 Grab GW µg/L 2.1 0.5 U 0.6 6.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 11/19/12 Grab GW µg/L 2.1 0.5 U 0.6 5.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 10/18/12 Grab GW µg/L 1.7 0.5 U 0.5 U 5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 10/18/12 Grab GW µg/L 1.7 0.5 U 0.5 5.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 9/18/12 Grab GW µg/L 0.84 J^ 0.5 U 0.21 JL 1.8 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 9/18/12 Grab GW µg/L 0.9 J^ 0.5 U 0.22 JL 2.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 8/6/12 Grab GW µg/L 2.3 0.5 U 0.5 U 6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 8/6/12 Grab GW µg/L 2.1 0.5 U 0.5 U 6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 7/16/12 Grab GW µg/L 1.8 0.5 U 0.5 U 4.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 7/16/12 Grab GW µg/L 1.9 0.5 U 0.5 4.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 6/20/12 Grab GW µg/L 2.8 0.5 U 0.69 6.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 6/20/12 Grab GW µg/L 2.6 0.5 U 0.76 5.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 5/20/12 Grab GW µg/L 1.9 0.5 U 0.56 5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 5/20/12 Grab GW µg/L 1.9 0.5 U 0.6 4.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 4/20/12 Grab GW µg/L 2.6 0.5 U 0.71 6.5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 4/20/12 Grab GW µg/L 2.7 J 0.5 U 0.75 J 6.9 J 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 3/19/12 Grab GW µg/L 2.1 0.5 U 0.53 6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 3/19/12 Grab GW µg/L 2.3 0.5 U 0.55 5.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 2/27/12 Grab GW µg/L 1.9 0.5 U 0.5 4.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 2/27/12 Grab GW µg/L 1.8 0.5 U 0.5 4.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 1/16/12 Grab GW µg/L 2.3 0.5 U 0.66 6.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 1/16/12 Grab GW µg/L 2.5 J 0.5 U 0.84 J 9.2 J 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 12/19/11 Grab GW µg/L 2.3 0.5 U 0.62 5.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 12/19/11 Grab GW µg/L 2.2 0.5 U 0.61 5.4 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 11/22/11 Grab GW µg/L 2.1 2 U 2 U 4.9 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 11/22/11 Grab GW µg/L 2.3 2 U 2 U 5.6 2 UD2E‐P1 (D2) D2 FAP SP‐1 NA 10/17/11 Grab GW µg/L 1.6 LJ 2 U 2 U 3.8 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 10/17/11 Grab GW µg/L 1.6 LJ 2 U 2 U 4 2 UD2E‐P1 (D2) D2 FAP SP‐1 NA 10/17/11 Grab GW µg/L 2 2 U 2 U 4.6 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 10/17/11 Grab GW µg/L 2 2 U 2 U 4.9 2 UD2E‐P1 (D2) D2 FAP SP‐1 NA 9/19/11 Grab GW µg/L 1.8 LJ 2 U 2 U 4 2 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 9/19/11 Grab GW µg/L 2.1 2 U 2 U 3.8 2 UD2E‐P1 (D2) D2 FAP SP‐1 NA 8/22/11 Grab GW µg/L 3.3 5 U 5 U 8.9 5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 8/22/11 Grab GW µg/L 3.1 5 U 5 U 8.9 5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 7/18/11 Grab GW µg/L 2.3 0.5 U 0.6 5.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 7/18/11 Grab GW µg/L 2.3 0.5 U 0.6 5.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 6/20/11 Grab GW µg/L 2.4 0.5 U 0.7 6 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 2 OF 64
011490
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 6/20/11 Grab GW µg/L 2.5 0.5 U 0.7 5.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 5/24/11 Grab GW µg/L 2.8 0.5 U 0.7 6.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 5/24/11 Grab GW µg/L 2.7 0.5 U 0.8 6.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 4/18/11 Grab GW µg/L 2.5 0.5 U 0.7 6.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 4/18/11 Grab GW µg/L 2.4 0.5 U 0.7 6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 12/14/10 Grab GW µg/L 2.3 0.5 U 0.66 5.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 12/14/10 Grab GW µg/L 2.4 0.5 U 0.69 5.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 9/23/10 Grab GW µg/L 1.6 0.5 U 0.5 U 4.4 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 9/23/10 Grab GW µg/L 1.5 0.5 U 0.5 U 4.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 6/22/10 Grab GW µg/L 1.9 0.5 U 0.6 5.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 6/22/10 Grab GW µg/L 2 0.5 U 0.6 5.5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 3/18/10 Grab GW µg/L 1.8 0.5 U 0.6 5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP NA 3/18/10 Grab GW µg/L 1.8 0.5 U 0.6 5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q110 NA 2/1/10 Grab GW µg/L 2 0.5 U 0.6 5.5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q110 NA 2/1/10 Grab GW µg/L 2.2 0.5 U 0.6 5.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 NA 11/30/09 Grab GW µg/L 1.8 0.5 U 0.5 U 4.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q409 NA 10/28/09 Grab GW µg/L 1.8 0.5 U 0.51 4.8 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q409 NA 10/28/09 Grab GW µg/L 2 0.5 U 0.54 5.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q309 NA 7/6/09 Grab GW µg/L 2.5 0.5 U 0.9 7.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q309 NA 7/6/09 Grab GW µg/L 2.6 0.5 U 0.9 8.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1‐Q209 NA 4/20/09 Grab GW µg/L 3 0.5 U 1 7.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 DUP‐Q209 NA 4/20/09 Grab GW µg/L 3.1 0.5 U 1 8.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 090212 NA 2/12/09 Grab GW µg/L 3.2 0.5 U 1.1 7.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 090212‐DUP NA 2/12/09 Grab GW µg/L 3.1 0.5 U 1 7.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 081111 NA 11/11/08 Grab GW µg/L 3 0.5 U 1 7.8 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 081111‐DUP NA 11/11/08 Grab GW µg/L 3 0.5 U 0.9 7.5 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080707 NA 7/7/08 Grab GW µg/L 3.4 0.5 U 1.2 8.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080414 NA 4/14/08 Grab GW µg/L 4.6 0.5 U 1.5 11 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080414‐DUP NA 4/14/08 Grab GW µg/L 4.6 0.5 U 1.5 12 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080218 NA 2/18/08 Grab GW µg/L 3.8 0.5 U 1.4 9.7 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 080218‐DUP NA 2/18/08 Grab GW µg/L 3.7 0.5 U 1.2 9.4 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 071029 NA 10/28/07 Grab GW µg/L 4.4 0.5 U 1.5 11.4 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 071029‐DUP NA 10/28/07 Grab GW µg/L 4.4 0.5 U 1.6 11.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 070823 NA 8/23/07 Grab GW µg/L 4.1 0.5 U 1.5 10 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 070602 NA 6/2/07 Grab GW µg/L 4.1 0.5 U 1.5 10.2 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 070602‐DUP NA 6/2/07 Grab GW µg/L 4.2 0.5 U 1.3 9.9 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 B07 NA 2/20/07 Grab GW µg/L 4.2 0.5 U 1.5 12 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 B07 Dup NA 2/20/07 Grab GW µg/L 4.3 0.5 U 1.5 12 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 C07 NA 2/20/07 Grab GW µg/L 4.1 0.5 U 1.4 12 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 C07 Dup NA 2/20/07 Grab GW µg/L 4.2 0.5 U 1.5 12.3 0.5 UD2E‐P1 (D2) D2 FAP SP‐107 NA 2/19/07 Grab GW µg/L 4.2 0.5 U 1.6 12.1 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 061016 NA 10/16/06 Grab GW µg/L 4.6 0.5 U 1.7 11.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 0600816 NA 8/16/06 Grab GW µg/L 5.6 0.5 U 1.9 13.6 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 0600719 NA 7/19/06 Grab GW µg/L 5.6 0.5 U 2.1 13.4 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060524 NA 5/24/06 Grab GW µg/L 4.7 0.5 U 1.9 12.8 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060329 NA 3/29/06 Grab GW µg/L 5 0.5 U 1 12 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 3 OF 64
011491
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodD2E‐P1 (D2) D2 FAP SP‐1 060308 NA 3/8/06 Grab GW µg/L 4.3 0.5 U 1.5 13 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060127 NA 1/27/06 Grab GW µg/L 4.6 0.5 U 2.3 12 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 060109 NA 1/9/06 Grab GW µg/L 6 0.5 U 2.5 13 0.5 UD2E‐P1 (D2) D2 FAP SP‐1 051130 NA 11/30/05 Grab GW µg/L 5 0.5 U 1.4 11 0.5 UD2E‐P1 (D2) D2 FAP Infl 102505 NA 10/25/05 Grab GW µg/L 6.6 0.5 U 2.7 14 0.5 UD2E‐P1 (D2) D2 FAP DUP 102505 NA 10/25/05 Grab GW µg/L 6.4 0.5 U 2.7 14 0.5 UD2E‐P1 (D2) D2 FAP Infl 102105 NA 10/21/05 Grab GW µg/L 5.3 0.5 U 2.2 12 0.5 UD2E‐P1 (D2) D2 FAP Infl 101905 NA 10/19/05 Grab GW µg/L 5.7 0.5 U 2.1 12 0.5 UD2E‐P1 (D2) D2 ASTP INFLUENT NA 3/17/05 Grab GW µg/L 6 0.5 U 2.4 15 0.5 UD2E‐P1 (D2) D2 ASTP INFLUENT NA 2/22/05 Grab GW µg/L 5.6 0.5 U 2.4 14 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT1 NA 1/5/05 Grab GW µg/L 5.7 0.5 U 2.5 13 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT2 NA 1/5/05 Grab GW µg/L 5.3 0.5 U 2.4 12 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT3 NA 1/5/05 Grab GW µg/L 4.9 0.5 U 2.3 13 0.5 UD2E‐P1 (D2) D2 Q105ASTPINFLUENT4 NA 1/5/05 Grab GW µg/L 5.4 0.5 U 2.4 12 0.5 U
DM‐01 (S) NA 5/10/2020 0:00 unknownDM‐01 (S) S FX085 NA 5/2/2000 0:00 BAIL GW µg/L 2 = 0.8 LJ 2 = 3 = 1 UDM‐01 (S) S FGG07 NA 8/3/1999 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 UDM‐01 (S) S FQ881 NA 11/12/1997 0:00 unknown GW µg/L 3 = 2 = 2 = 6 = 1 UDM‐01 (S) S FW896 NA 12/12/1996 0:00 unknown GW µg/L 2 = 1 = 2 = 7 = 1 UDM‐01 (S) S 930949‐3 NA 9/28/1993 0:00 unknown GW µg/L 4.9 = 1.8 = 3 = 4.5 = <0.2DM‐01 (S) S 930933‐1 NA 9/22/1993 0:00 unknown GW µg/L 3.6 = 1.6 = 2.9 = 3.6 = <0.2
DM‐02 (I) NA 5/10/2020 0:00 unknownDM‐02 (I) I FGG55 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 6 = 2 U 2 = 29 = 2 UDM‐02 (I) I FGG08 NA 8/3/1999 0:00 unknown GW µg/L 9 = 1 U 3 = 54 = 1 UDM‐02 (I) I FQ894 NA 11/17/1997 0:00 unknown GW µg/L 8 = 1 U 3 = 47 = 1 UDM‐02 (I) I FW889 NA 12/11/1996 0:00 unknown GW µg/L 8 = 1 U 3 = 42 D NDDM‐02 (I) I 931057‐3 NA 10/28/1993 0:00 unknown GW µg/L 5.9 = <0.2 3.5 = 43 = <0.2DM‐02 (I) I 930949‐2 NA 9/28/1993 0:00 unknown GW µg/L 6.9 = <0.2 3.5 = 43 = <0.2
DM‐03 (I) NA 5/10/2020 0:00 unknownDM‐03 (I) I FGS96 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 4 = 1 U 2 = 11 = 1 UDM‐03 (I) I FGF96 NA 8/3/1999 0:00 unknown GW µg/L 5 = 1 U 2 = 18 = 1 UDM‐03 (I) I FQ893 NA 11/17/1997 0:00 unknown GW µg/L 5 = 1 U 2 = 20 = 1 UDM‐03 (I) I FW890 NA 12/11/1996 0:00 unknown GW µg/L 5 = 1 U 2 = 24 = NDDM‐03 (I) I 930949‐1 NA 9/28/1993 0:00 unknown GW µg/L 5.8 = <0.2 3.2 = 31 = <0.2DM‐03 (I) I 930949‐5 NA 9/28/1993 0:00 unknown GW µg/L 6.3 = <0.2 3.5 = 32 = <0.2
DM‐04 (S) NA 5/10/2020 0:00 unknownDM‐04 (S) S FX089 NA 5/2/2000 0:00 BAIL GW µg/L 1 = 1 = 0.8 LJ 0.6 LJ 1 UDM‐04 (S) S FGF97 NA 8/3/1999 0:00 unknown GW µg/L 0.9 LJ 0.8 LJ 1 = 0.7 LJ 1 UDM‐04 (S) S FQ877 NA 11/12/1997 0:00 unknown GW µg/L 0.9 J 15 = 0.8 J 0.9 J 1 UDM‐04 (S) S FW892 NA 12/11/1996 0:00 unknown GW µg/L 2 = 0.6 J 2 = 0.8 J 1 UDM‐04 (S) S 930949‐4 NA 9/29/1993 0:00 unknown GW µg/L 1.5 = 5.6 = 2 = 1.1 = <0.2
DM‐05 (S) NA 5/10/2020 0:00 unknownDM‐05 (S) S DM‐05‐S‐8‐022014 DM‐O5‐S‐8 2/18/2014 8:18 PDB GW µg/L 0.5 U 0.7 = 0.5 U 0.5 U 0.5 UDM‐05 (S) S F6PA0 DM‐O5‐S‐8 2/12/2013 0:00 PDB GW µg/L 0.25 LJ 1.1 = 0.5 U 0.32 LJ 0.5 UDM‐05 (S) S F5G69 DM‐05‐S‐8 2/28/2012 8:35 PDB GW µg/L 0.33 LJ 0.5 U 0.1 LJ 0.36 LJ 0.5 UDM‐05 (S) S DM‐05‐S‐8‐Q111 DM‐05‐S‐8 2/16/2011 8:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 4 OF 64
011492
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodDM‐05 (S) S F3LR9 DM‐05‐S‐8‐Q310‐FD 9/3/2010 9:10 PDB GW µg/L 0.47 LJ 0.5 U 0.5 U 0.52 = 0.5 UDM‐05 (S) S F3LR8 DM‐05‐S‐8‐Q310 9/3/2010 9:05 PDB GW µg/L 0.55 = 0.5 U 0.5 U 0.58 = 0.5 UDM‐05 (S) S F3LR7 DM‐05‐S‐5‐Q310 9/3/2010 9:00 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 0.51 = 0.5 UDM‐05 (S) S F3LR6 DM‐05‐S‐2‐Q310 9/3/2010 8:55 PDB GW µg/L 0.5 U 3.5 = 0.5 U 1.2 = 0.5 UDM‐05 (S) S DM‐05‐S‐8_100201‐FD DM‐05‐S‐8 2/1/2010 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐05 (S) S DM‐05‐S‐8_100201 DM‐05‐S‐8 2/1/2010 10:32 PDB GW µg/L 0.5 = 0.5 U 0.5 U 0.5 U 0.5 UDM‐05 (S) S F3B47 DM‐05‐S‐8 10/26/2009 8:45 PDB GW µg/L 0.54 = 0.5 U 0.32 LJ 0.48 LJ 0.5 UDM‐05 (S) S F3B45 DM‐05‐S‐5 10/26/2009 8:41 PDB GW µg/L 0.43 LJ 0.5 U 0.28 LJ 0.44 LJ 0.5 UDM‐05 (S) S F3B44 DM‐05‐S‐2 10/26/2009 8:38 PDB GW µg/L 0.5 U 1.5 = 0.5 U 0.51 = 0.5 UDM‐05 (S) S FW573 NA 2/1/2000 0:00 unknown GW µg/L 0.9 LJ 4 = 0.9 LJ 1 = 1 UDM‐05 (S) S FGR75 NA 11/3/1999 0:00 unknown GW µg/L 0.6 LJ 2 = 3 = 1 = 1 UDM‐05 (S) S FQ813 NA 11/18/1997 0:00 unknown GW µg/L 2 = 10 = 1 = 3 = 1 UDM‐05 (S) S 930948‐1 NA 9/29/1993 0:00 unknown GW µg/L 2.2 = 4.3 = 2 = 2.4 = <0.2
DM‐06 (I1/I2) NA 5/10/2020 0:00 unknownDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐2‐022014 DM‐06‐I1/I2‐2 2/18/2014 8:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.9 = 0.5 UDM‐06 (I1/I2) I1/I2 F6PA2 DM‐06‐I1/I2‐2‐FD 2/12/2013 0:00 PDB GW µg/L 0.49 LJ 0.5 U 0.16 LJ 0.99 = 0.5 UDM‐06 (I1/I2) I1/I2 F6PA1 DM‐06‐I1/I2‐2 2/12/2013 0:00 PDB GW µg/L 0.54 = 0.5 U 0.18 LJ 1.2 = 0.5 UDM‐06 (I1/I2) I1/I2 F5G70 DM‐06‐I1/I2‐2 2/27/2012 9:38 PDB GW µg/L 0.51 = 0.5 U 0.2 LJ 1.1 = 0.5 UDM‐06 (I1/I2) I1/I2 F3S31 DM‐06‐I1/I2‐2 2/15/2011 8:02 PDB GW µg/L 0.98 = 0.5 U 0.56 = 3.7 J 0.5 UDM‐06 (I1/I2) I1/I2 F3LS6 DM‐06‐I1/I2‐27‐Q310 9/3/2010 11:55 PDB GW µg/L 0.77 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS5 DM‐06‐I1/I2‐22‐Q310 9/3/2010 11:50 PDB GW µg/L 0.78 = 0.5 U 0.5 U 1.9 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS4 DM‐06‐I1/I2‐17‐Q310‐FD 9/3/2010 11:40 PDB GW µg/L 0.73 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS3 DM‐06‐I1/I2‐17‐Q310 9/3/2010 11:35 PDB GW µg/L 0.75 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS2 DM‐06‐I1/I2‐12‐Q310 9/3/2010 11:30 PDB GW µg/L 0.72 = 0.5 U 0.35 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS1 DM‐06‐I1/I2‐7‐Q310 9/3/2010 11:25 PDB GW µg/L 0.7 = 0.5 U 0.32 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3LS0 DM‐06‐I1/I2‐2‐Q310 9/3/2010 11:20 PDB GW µg/L 0.7 = 0.5 U 0.35 LJ 2.1 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐17_100202‐FD DM‐06‐I1/I2‐17 2/2/2010 9:01 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐27_100202 DM‐06‐I1/I2‐27 2/2/2010 8:07 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐22_100202 DM‐06‐I1/I2‐22 2/2/2010 8:05 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐17_100202 DM‐06‐I1/I2‐17 2/2/2010 8:01 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐12_100202 DM‐06‐I1/I2‐12 2/2/2010 7:59 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐7_100202 DM‐06‐I1/I2‐7 2/2/2010 7:57 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2.1 = 0.5 UDM‐06 (I1/I2) I1/I2 DM‐06‐I1/I2‐2_100202 DM‐06‐I1/I2‐2 2/2/2010 7:55 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.9 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B53 DM‐06‐I1/I2‐27 10/28/2009 8:20 PDB GW µg/L 0.71 = 0.5 U 0.32 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B52 DM‐06‐I1/I2‐22 10/28/2009 8:16 PDB GW µg/L 0.69 = 0.5 U 0.33 LJ 1.7 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B51 DM‐06‐I1/I2‐17 10/28/2009 8:12 PDB GW µg/L 0.71 = 0.5 U 0.33 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B50 DM‐06‐I1/I2‐12 10/28/2009 8:08 PDB GW µg/L 0.73 = 0.5 U 0.34 LJ 1.8 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B49 DM‐06‐I1/I2‐7 10/28/2009 8:04 PDB GW µg/L 0.7 = 0.5 U 0.33 LJ 1.7 = 0.5 UDM‐06 (I1/I2) I1/I2 F3B48 DM‐06‐I1/I2‐2 10/28/2009 8:00 PDB GW µg/L 0.68 = 0.5 U 0.32 LJ 1.7 = 0.5 UDM‐06 (I1/I2) I FW589 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 2 = 1 U 1 = 6 = 1 UDM‐06 (I1/I2) I FW552 NA 2/8/2000 0:00 unknown GW µg/L 2 = 1 U 1 = 5 = 1 UDM‐06 (I1/I2) I FGR60 NA 11/1/1999 0:00 unknown GW µg/L 3 = 1 U 4 = 4 = 1 UDM‐06 (I1/I2) I FGF78 NA 7/30/1999 0:00 unknown GW µg/L 2 = 1 U 2 = 7 = 1 UDM‐06 (I1/I2) I FQ858 NA 11/5/1997 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 UDM‐06 (I1/I2) I FQ859 NA 11/5/1997 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 UDM‐06 (I1/I2) I FW503 NA 12/17/1996 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = 1 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 5 OF 64
011493
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodDM‐06 (I1/I2) I 931003‐2 NA 10/2/1993 0:00 unknown GW µg/L 2.9 = <0.2 2.1 = 6.8 = NDDM‐06 (I1/I2) I 931003‐1 NA 10/2/1993 0:00 unknown GW µg/L 3 = <0.2 2.3 = 7.2 = ND
DM‐07 (I1/I2) NA 5/10/2020 0:00 unknownDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐27‐022014 DM‐07‐I1/I2‐27 2/17/2014 13:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐12‐022014 DM‐07‐I1/I2‐12 2/17/2014 13:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F6PA3 DM‐07‐I1/I2‐12 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F6PA4 DM‐07‐I1/I2‐27 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F6CA1 DM‐07‐I1/I2‐27 8/20/2012 8:35 PDB GW µg/L 0.5 U 0.055 LJ 0.5 U 0.059 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F6CA0 DM‐07‐I1/I2‐12 8/20/2012 8:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.085 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F5G75 DM‐07‐I1/I2‐27 2/28/2012 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G74 DM‐07‐I1/I2‐22 2/28/2012 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G72 DM‐07‐I1/I2‐17 2/28/2012 10:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G71 DM‐07‐I1/I2‐12 2/28/2012 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G76 DM‐07‐I1/I2‐7 2/28/2012 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F5G73 DM‐07‐I1/I2‐2 2/28/2012 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F4EA2 DM‐07‐I1/I2‐12‐Q311 8/22/2011 9:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UDM‐07 (I1/I2) I1/I2 F4EA1 DM‐07‐I1/I2‐7‐Q311 8/22/2011 9:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UDM‐07 (I1/I2) I1/I2 F4EA0 DM‐07‐I1/I2‐2‐Q311 8/22/2011 9:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UDM‐07 (I1/I2) I1/I2 F3S35 DM‐07‐I1/I2‐12 2/15/2011 8:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐07 (I1/I2) I1/I2 F3S34 DM‐07‐I1/I2‐7 2/15/2011 8:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐07 (I1/I2) I1/I2 F3S33 DM‐07‐I1/I2‐2 2/15/2011 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐07 (I1/I2) I1/I2 F3S32 DM‐07‐I1/I2‐2 2/15/2011 8:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.72 J 0.5 UDM‐07 (I1/I2) I1/I2 F3LT2 DM‐07‐I1/I2‐27‐Q310 9/3/2010 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.37 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LT1 DM‐07‐I1/I2‐22‐Q310 9/3/2010 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LT0 DM‐07‐I1/I2‐17‐Q310 9/3/2010 10:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LS9 DM‐07‐I1/I2‐12‐Q310 9/3/2010 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.37 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LS8 DM‐07‐I1/I2‐7‐Q310 9/3/2010 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.34 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3LS7 DM‐07‐I1/I2‐2‐Q310 9/3/2010 10:20 PDB GW µg/L 0.19 LJ 0.5 U 0.5 U 0.32 LJ 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐27_100202 DM‐07‐I1/I2‐27 2/2/2010 8:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐22_100202 DM‐07‐I1/I2‐22 2/2/2010 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐17_100202 DM‐07‐I1/I2‐17 2/2/2010 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐12_100202 DM‐07‐I1/I2‐12 2/2/2010 8:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐7_100202 DM‐07‐I1/I2‐7 2/2/2010 8:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 DM‐07‐I1/I2‐2_100202 DM‐07‐I1/I2‐2 2/2/2010 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐07 (I1/I2) I1/I2 F3B32 DM‐07‐I1/I2‐27 10/26/2009 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B31 DM‐07‐I1/I2‐22 10/26/2009 10:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B30 DM‐07‐I1/I2‐17 10/26/2009 9:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.3 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B29 DM‐07‐I1/I2‐12 10/26/2009 9:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.27 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B28 DM‐07‐I1/I2‐7 10/26/2009 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.3 LJ 0.5 UDM‐07 (I1/I2) I1/I2 F3B27 DM‐07‐I1/I2‐2 10/26/2009 9:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐07 (I1/I2) I FGS95 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 1 = 1 U 1 U 1 = 1 UDM‐07 (I1/I2) I FGF76 NA 7/30/1999 0:00 unknown GW µg/L 1 = 1 U 1 U 1 = 1 UDM‐07 (I1/I2) I FQ847 NA 11/3/1997 0:00 unknown GW µg/L 1 = 1 U 1 U 1 = 1 UDM‐07 (I1/I2) I FW876 NA 12/9/1996 0:00 unknown GW µg/L 2 = 1 U 0.6 J 2 = NDDM‐07 (I1/I2) I 931013‐1 NA 10/7/1993 0:00 unknown GW µg/L 2.7 = <0.2 0.8 = 1.3 = <0.2DM‐07 (I1/I2) I 931001‐1 NA 10/1/1993 0:00 unknown GW µg/L 1.7 = <0.2 0.4 = 0.7 = <0.2
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 6 OF 64
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TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodDM‐08 (I1/I2) NA 5/10/2020 0:00 unknown
DM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22‐022014 DM‐08‐I1/I2‐22 2/18/2014 10:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12‐022014 DM‐08‐I1/I2‐12 2/18/2014 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F6PA6 DM‐08‐I1/I2‐22 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.16 LJ 0.5 U 0.26 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F6PA5 DM‐08‐I1/I2‐12 2/12/2013 0:00 PDB GW µg/L 0.14 LJ 0.22 LJ 0.5 U 0.27 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F5G79 DM‐08‐I1/I2‐22‐FD 2/27/2012 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F5G78 DM‐08‐I1/I2‐22 2/27/2012 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F5G77 DM‐08‐I1/I2‐12 2/27/2012 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F3S37 DM‐08‐I1/I2‐22 2/15/2011 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐08 (I1/I2) I1/I2 F3S36 DM‐08‐I1/I2‐12 2/15/2011 8:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22_100201 DM‐08‐I1/I2‐22 2/1/2010 14:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12_100201 DM‐08‐I1/I2‐12 2/1/2010 14:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22‐Q209 DM‐08‐I1/I2‐22 4/20/2009 10:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12‐Q209 DM‐08‐I1/I2‐12 4/20/2009 10:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F2913 DM‐08‐I1/I2‐2 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2916 DM‐08‐I1/I2‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2915 DM‐08‐I1/I2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2917 DM‐08‐I1/I2‐27 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.31 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2918 DM‐08‐I1/I2‐17 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.35 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F2919 DM‐08‐I1/I2‐22 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐22‐Q407 DM‐08‐I1/I2‐22 10/2/2007 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 DM‐08‐I1/I2‐12‐Q407 DM‐08‐I1/I2‐12 10/2/2007 8:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1NR4 DM‐08‐I‐27 7/12/2005 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1NR3 DM‐08‐I‐22 7/12/2005 8:54 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.44 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1NR2 DM‐08‐I‐17 7/12/2005 8:50 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1NR0 DM‐08‐I‐12 7/12/2005 8:46 PDB GW µg/L 0.26 LJ 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1NQ9 DM‐08‐I‐7 7/12/2005 8:42 PDB GW µg/L 0.26 LJ 0.5 U 0.5 U 0.38 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1NQ8 DM‐08‐I‐2 7/12/2005 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐08 (I1/I2) I1/I2 F1DL7 DM‐08‐I‐27 4/18/2005 10:07 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 0.32 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL6 DM‐08‐I‐22 4/18/2005 10:06 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL5 DM‐08‐I‐17 4/18/2005 10:05 PDB GW µg/L 0.3 LJ 0.5 U 0.5 U 0.35 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL3 DM‐08‐I‐12 4/18/2005 10:03 PDB GW µg/L 0.32 LJ 0.5 U 0.1 LJ 0.35 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL2 DM‐08‐I‐7 4/18/2005 10:02 PDB GW µg/L 0.18 LJ 0.5 U 0.5 U 0.21 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F1DL1 DM‐08‐I‐2 4/18/2005 10:00 PDB GW µg/L 0.24 LJ 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17G2 DM‐08‐I‐27 11/10/2004 10:15 PDB GW µg/L 0.34 LJ 0.5 U 0.5 U 0.46 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17G1 DM‐08‐I‐22 11/10/2004 10:13 PDB GW µg/L 0.37 LJ 0.5 U 0.5 U 0.44 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17G0 DM‐08‐I‐17 11/10/2004 10:11 PDB GW µg/L 0.33 LJ 0.5 U 0.5 U 0.38 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17F8 DM‐08‐I‐12 11/10/2004 10:07 PDB GW µg/L 0.35 LJ 0.5 U 0.5 U 0.41 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17F7 DM‐08‐I‐7 11/10/2004 10:05 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 0.36 LJ 0.5 UDM‐08 (I1/I2) I1/I2 F17F6 DM‐08‐I‐2 11/10/2004 10:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐08 (I1/I2) I1/I2 DM08‐020221 NA 2/21/2002 15:15 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UDM‐08 (I1/I2) I FW583 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 0.7 LJ 1 U 1 U 1 = 1 UDM‐08 (I1/I2) I FW549 NA 2/8/2000 0:00 unknown GW µg/L 0.8 LJ 1 U 1 U 3 = 1 UDM‐08 (I1/I2) I FGR59 NA 11/1/1999 0:00 unknown GW µg/L 0.8 LJ 1 U 0.5 LJ 1 = 1 UDM‐08 (I1/I2) I FGF86 NA 8/2/1999 0:00 unknown GW µg/L 0.5 LJ 1 U 1 U 2 = 1 UDM‐08 (I1/I2) I FQ854 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 0.7 J 1 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 7 OF 64
011495
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodDM‐08 (I1/I2) I FW878 NA 12/9/1996 0:00 unknown GW µg/L 1 U 1 U 1 U 0.5 J NDDM‐08 (I1/I2) I 931019‐1 NA 10/8/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
DM‐09 (S) NA 5/10/2020 0:00 unknownDM‐09 (S) S DM‐09‐S‐7‐022014 DM‐09‐S‐7 2/18/2014 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S F6PA7 DM‐09‐S‐7 2/12/2013 0:00 PDB GW µg/L 0.47 LJ 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S F5G80 DM‐09‐S‐7 2/27/2012 9:19 PDB GW µg/L 0.45 LJ 0.5 U 0.5 U 0.25 LJ 0.5 UDM‐09 (S) S F3S38 DM‐09‐S‐5 2/15/2011 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UDM‐09 (S) S DM‐09‐S‐7_100201 DM‐09‐S‐7 2/1/2010 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM‐09‐S‐7‐Q209 DM‐09‐S‐7 4/20/2009 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM‐09‐S‐7‐Q408 DM‐09‐S‐7 10/6/2008 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM‐09‐S‐7‐Q407 DM‐09‐S‐7 10/2/2007 10:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 = 0.5 UDM‐09 (S) S F2641 DM‐09‐S‐7 8/28/2006 13:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S F1NR7 DM‐09‐S‐12 7/12/2005 8:30 PDB GW µg/L 0.49 LJ 0.15 LJ 0.25 LJ 0.93 = 0.5 UDM‐09 (S) S F1NR6 DM‐09‐S‐7 7/12/2005 8:28 PDB GW µg/L 0.5 = 0.16 LJ 0.28 LJ 0.93 = 0.5 UDM‐09 (S) S F1DL8 DM‐09‐S‐2 4/18/2005 9:38 PDB GW µg/L 3.1 UJv 3.1 U 3.1 UJv 3.1 U 3.1 UDM‐09 (S) S F1DL9 DM‐09‐S‐7 4/18/2005 9:36 PDB GW µg/L 0.28 LJv 0.5 U 0.12 LJv 0.4 LJ 0.5 UDM‐09 (S) S F1DM0 DM‐09‐S‐12 4/18/2005 9:34 PDB GW µg/L 0.25 LJv 0.5 U 0.12 LJv 0.38 LJ 0.5 UDM‐09 (S) S F17G5 DM‐09‐S‐12 11/10/2004 9:56 PDB GW µg/L 0.47 LJ 0.5 U 0.5 U 0.55 J 0.5 UDM‐09 (S) S F17G4 DM‐09‐S‐7 11/10/2004 9:54 PDB GW µg/L 0.42 LJv 0.5 U 0.5 UJv 0.53 J 0.5 UDM‐09 (S) S F17G3 DM‐09‐S‐2 11/10/2004 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UDM‐09 (S) S DM09‐020221 NA 2/21/2002 16:30 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐09 (S) S FX081 NA 5/2/2000 0:00 BAIL GW µg/L 2 U 2 U 2 U 2 U 2 UDM‐09 (S) S FGF85 NA 8/2/1999 0:00 unknown GW µg/L 0.5 LJ 1 U 1 U 1 = 1 UDM‐09 (S) S FQ856 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UDM‐09 (S) S FQ855 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 0.9 J 1 UDM‐09 (S) S 931019‐2 NA 10/8/1993 0:00 unknown GW µg/L 0.3 = <0.2 <0.2 0.4 = <0.2
DM‐10 (S) NA 5/10/2020 0:00 unknownDM‐10 (S) S FGF68 NA 7/29/1999 0:00 unknown GW µg/L 1 = 1 U 1 U 2 = 1 UDM‐10 (S) S FQ846 NA 11/3/1997 0:00 unknown GW µg/L 1 = 1 U 1 U 2 = 1 UDM‐10 (S) S FW877 NA 12/9/1996 0:00 unknown GW µg/L 2 = 1 U 0.5 J 2 = NDDM‐10 (S) S 931013‐2 NA 10/7/1993 0:00 unknown GW µg/L 0.6 = <0.2 <0.2 0.9 = <0.2
DM‐11 (S) NA 5/10/2020 0:00 unknownDM‐11 (S) S FGF45 NA 7/27/1999 0:00 unknown GW µg/L 0.9 J 1 U 1 = 1 U 1 UDM‐11 (S) S FQ866 NA 11/6/1997 0:00 unknown GW µg/L 1 = 1 U 1 = 1 U 1 UDM‐11 (S) S FW507 NA 12/17/1996 0:00 unknown GW µg/L 1 = 1 U 1 = 1 U 1 UDM‐11 (S) S 931057‐2 NA 10/28/1993 0:00 unknown GW µg/L 2.1 = <0.2 2.5 = 0.9 = <0.2DM‐11 (S) S 931019‐3 NA 10/8/1993 0:00 unknown GW µg/L 2.4 = <0.2 1.8 = 0.6 = <0.2
DM‐12 (I1) NA 5/10/2020 0:00 unknownDM‐12 (I1) I1 F6PA8 DM‐12‐I1‐22 2/19/2013 0:00 PDB GW µg/L 2 = 0.5 U 0.39 LJ 2.6 = 0.5 UDM‐12 (I1) I1 F5G81 DM‐12‐I1‐22 2/27/2012 13:00 PDB GW µg/L 2 = 0.5 U 0.5 U 2.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐22‐Q111 DM‐12‐I1‐22 2/14/2011 12:40 PDB GW µg/L 1.8 = 0.5 U 0.5 U 2.8 = 0.5 UDM‐12 (I1) I1 F3LT7 DM‐12‐I1‐7‐Q310 9/3/2010 10:00 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3LT9 DM‐12‐I1‐27‐Q310 9/3/2010 9:55 PDB GW µg/L 2 = 0.5 U 0.39 LJ 3.2 = 0.5 UDM‐12 (I1) I1 F3LT8 DM‐12‐I1‐22‐Q310 9/3/2010 9:50 PDB GW µg/L 1.9 = 0.5 U 0.33 LJ 3.3 = 0.5 UDM‐12 (I1) I1 F3LT6 DM‐12‐I1‐17‐Q310 9/3/2010 9:45 PDB GW µg/L 1.9 = 0.5 U 0.34 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3LT5 DM‐12‐I1‐12‐Q310 9/3/2010 9:40 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 3.2 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 8 OF 64
011496
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodDM‐12 (I1) I1 F3LT4 DM‐12‐I1‐2‐Q310‐FD 9/3/2010 9:35 PDB GW µg/L 2 = 0.5 U 0.37 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3LT3 DM‐12‐I1‐2‐Q310 9/3/2010 9:30 PDB GW µg/L 2.1 = 0.5 U 0.43 LJ 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐2_100201‐FD DM‐12‐I1‐2 2/1/2010 9:23 PDB GW µg/L 2.2 = 0.5 U 0.5 U 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐2_100201 DM‐12‐I1‐2 2/1/2010 8:23 PDB GW µg/L 2.2 = 0.5 U 0.5 U 3.5 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐7_100201 DM‐12‐I1‐7 2/1/2010 8:20 PDB GW µg/L 1.9 = 0.5 U 0.5 U 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐12_100201 DM‐12‐I1‐12 2/1/2010 8:18 PDB GW µg/L 2.1 = 0.5 U 0.5 U 3.4 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐17_100201 DM‐12‐I1‐17 2/1/2010 8:16 PDB GW µg/L 2.3 = 0.5 U 0.5 U 3.7 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐22_100201 DM‐12‐I1‐22 2/1/2010 8:14 PDB GW µg/L 2.1 = 0.5 U 0.5 U 3.8 = 0.5 UDM‐12 (I1) I1 DM‐12‐I1‐27_100201 DM‐12‐I1‐27 2/1/2010 8:10 PDB GW µg/L 2.1 = 0.5 U 0.5 U 3.7 = 0.5 UDM‐12 (I1) I1 F3B60 DM‐12‐I1‐27 10/26/2009 11:37 PDB GW µg/L 2.5 = 0.5 U 0.43 LJ 3.4 = 0.5 UDM‐12 (I1) I1 F3B59 DM‐12‐I1‐22 10/26/2009 11:34 PDB GW µg/L 2.4 = 0.5 U 0.43 LJ 3.4 = 0.5 UDM‐12 (I1) I1 F3B58 DM‐12‐I1‐17 10/26/2009 11:31 PDB GW µg/L 2.3 = 0.5 U 0.43 LJ 3.2 = 0.5 UDM‐12 (I1) I1 F3B57 DM‐12‐I1‐12 10/26/2009 11:28 PDB GW µg/L 2.4 = 0.5 U 0.49 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3B56 DM‐12‐I1‐7 10/26/2009 11:23 PDB GW µg/L 2.4 = 0.5 U 0.46 LJ 3.1 = 0.5 UDM‐12 (I1) I1 F3B55 DM‐12‐I1‐2 10/26/2009 11:20 PDB GW µg/L 2.5 = 0.5 U 0.47 LJ 3.2 = 0.5 UDM‐12 (I1) I FGS97 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 11 = 2 U 4 = 42 = 2 UDM‐12 (I1) I FW577 NA 2/1/2000 0:00 unknown GW µg/L 7 = 1 U 4 = 15 = 1 UDM‐12 (I1) I FW578 NA 2/1/2000 0:00 unknown GW µg/L 7 = 1 U 4 = 15 = 1 UDM‐12 (I1) I FGR80 NA 11/4/1999 0:00 unknown GW µg/L 13 = 1 U 11 = 33 = 1 UDM‐12 (I1) I FGF44 NA 7/27/1999 0:00 unknown GW µg/L 13 = 1 U 6 = 53 = 1 UDM‐12 (I1) I FGF43 NA 7/27/1999 0:00 unknown GW µg/L 13 = 1 U 6 = 54 = 1 UDM‐12 (I1) I FQ892 NA 11/13/1997 0:00 unknown GW µg/L 16 = 1 U 7 = 57 = 1 UDM‐12 (I1) I FW505 NA 12/17/1996 0:00 unknown GW µg/L 12 = 1 U 6 = 42 = 1 UDM‐12 (I1) I FW506 NA 12/17/1996 0:00 unknown GW µg/L 12 = 1 U 6 = 42 = 1 UDM‐12 (I1) I 931057‐5 NA 10/28/1993 0:00 unknown GW µg/L 8.6 = <0.2 3.1 = 70 = <0.2DM‐12 (I1) I 931057‐1 NA 10/28/1993 0:00 unknown GW µg/L 9.1 = <0.2 3.6 = 72 = <0.2DM‐12 (I1) I 931025‐1 NA 10/13/1993 0:00 unknown GW µg/L 5.3 = <0.2 1.6 = 53 = <0.2
DM‐13 (D1) NA 5/10/2020 0:00 unknownDM‐13 (D1) D1 FW586 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D1) D1 FQ878 NA 11/12/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D1) D1 FW502 NA 12/16/1996 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D1) D1 931116‐1 NA 11/5/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D1) D1 931116‐2 NA 11/5/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D1) D1 931040‐5 NA 10/19/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D1) D1 931039‐1 NA 10/18/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
DM‐13 (D2) NA 5/10/2020 0:00 unknownDM‐13 (D2) D2 FGS85 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FGS86 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FGF64 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FGF59 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 FQ875 NA 11/12/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UDM‐13 (D2) D2 970003‐9 NA 1/16/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U NDDM‐13 (D2) D2 931123‐5 NA 11/8/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 NDDM‐13 (D2) D2 931040‐4 NA 10/19/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2DM‐13 (D2) D2 931040‐6 NA 10/19/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
DM‐13 (I) NA 5/10/2020 0:00 unknown
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 9 OF 64
011497
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodDM‐13 (I) I FGS87 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 10 = 5 U 5 U 48 = 5 UDM‐13 (I) I FW572 NA 2/1/2000 0:00 unknown GW µg/L 13 = 1 U 3 = 37 = 1 UDM‐13 (I) I FGR83 NA 11/4/1999 0:00 unknown GW µg/L 15 = 2 U 6 = 47 = 2 UDM‐13 (I) I FGG00 NA 8/3/1999 0:00 unknown GW µg/L 12 = 1 U 3 = 64 = 1 UDM‐13 (I) I FGF99 NA 8/3/1999 0:00 unknown GW µg/L 13 = 1 U 3 = 69 = 1 UDM‐13 (I) I FQ880 NA 11/12/1997 0:00 unknown GW µg/L 11 = 1 U 2 = 86 = 1 UDM‐13 (I) I FQ879 NA 11/12/1997 0:00 unknown GW µg/L 10 = 5 U 5 U 76 = 5 UDM‐13 (I) I FW900 NA 12/16/1996 0:00 unknown GW µg/L 9 = 1 U 2 = 58 = 1 UDM‐13 (I) I 931057‐4 NA 10/28/1993 0:00 unknown GW µg/L 4.3 = <0.2 1 = 50 = <0.2DM‐13 (I) I 931040‐3 NA 10/19/1993 0:00 unknown GW µg/L 3.2 = <0.2 0.5 = 33 = <0.2
DM‐13 (S) NA 5/10/2020 0:00 unknownDM‐13 (S) S FX086 NA 5/2/2000 0:00 BAIL GW µg/L 2 = 2 = 1 = 3 = 1 UDM‐13 (S) S FW560 NA 2/9/2000 0:00 unknown GW µg/L 1 = 1 = 1 = 2 = 1 UDM‐13 (S) S FGR72 NA 11/3/1999 0:00 unknown GW µg/L 2 = 1 = 3 = 3 = 1 UDM‐13 (S) S FGF98 NA 8/3/1999 0:00 unknown GW µg/L 2 = 1 = 1 = 3 = 1 UDM‐13 (S) S FQ883 NA 11/12/1997 0:00 unknown GW µg/L 2 = 2 = 2 = 4 = 1 UDM‐13 (S) S FW899 NA 12/16/1996 0:00 unknown GW µg/L 2 = 2 = 3 = 4 = 1 UDM‐13 (S) S 931040‐2 NA 10/19/1993 0:00 unknown GW µg/L 2.6 = <0.2 2.4 = 6 = <0.2
FH‐MW4 (S) NA 5/10/2020 0:00 unknownFH‐MW4 (S) S FW580 NA 5/1/2000 0:00 BAIL GW µg/L 1 = 1 U 0.5 LJ 5 = 1 UFH‐MW4 (S) S FW581 NA 5/1/2000 0:00 BAIL GW µg/L 2 = 1 U 0.7 LJ 6 = 1 UFH‐MW4 (S) S FW550 NA 2/8/2000 0:00 unknown GW µg/L 1 = 1 U 0.6 LJ 5 = 1 UFH‐MW4 (S) S FGR61 NA 11/1/1999 0:00 unknown GW µg/L 2 = 1 U 2 = 5 = 1 UFH‐MW4 (S) S FGF71 NA 7/29/1999 0:00 unknown GW µg/L 1 = 1 U 0.7 LJ 5 = 1 U
FHMW‐5 (S) NA 5/10/2020 0:00 unknownFHMW‐5 (S) S FEF78 NA 8/5/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
FSB‐1 (S) NA 5/10/2020 0:00 unknownFSB‐1 (S) S FEF88 NA 8/12/1998 0:00 unknown GW µg/L 5 U 5 U 5 U 5 U 5 U
GP‐01 NA 5/10/2020 0:00 unknownGP‐01 unknown FW826 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐01 unknown FW827 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐02 unknown NA 5/10/2020 0:00 unknownGP‐02 unknown FW833 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐02 unknown FW830 NA 8/19/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐03 unknown NA 5/10/2020 0:00 unknownGP‐03 unknown FW844 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐03 unknown FW845 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐03 unknown FW847 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐04 unknown NA 5/10/2020 0:00 unknownGP‐04 unknown FW837 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐04 unknown FW838 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐05 unknown NA 5/10/2020 0:00 unknownGP‐05 unknown FW842 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UGP‐05 unknown FW843 NA 8/20/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
GP‐06 unknown NA 5/10/2020 0:00 unknownGP‐06 unknown FW850 NA 8/21/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 10 OF 64
011498
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodHSM‐I2‐4 NA 5/10/2020 0:00 unknown
HSM‐I2‐4 I2 F3LW1 HSM‐I2‐4‐Q310 8/31/2010 15:15 PDB GW µg/L 2.6 = 0.5 U 0.76 = 8.8 = 0.5 UHSM‐I2‐4 I2 F1D95 HSM‐I2‐4 4/19/2005 13:05 LFS GW µg/L 4.3 = 1 U 1.1 = 15 = 1 U
HSM‐I2‐5 NA 5/10/2020 0:00 unknownHSM‐I2‐5 I2 HSM‐I2‐5‐17‐022014 HSM‐I2‐5‐17 2/18/2014 8:50 PDB GW µg/L 5.9 = 0.5 U 0.8 = 17.9 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐0813 HSM‐I2‐5‐17 8/12/2013 11:00 PDB WG µg/L 6.2 = 0.5 U 0.9 = 23.2 = 0.5 UHSM‐I2‐5 I2 F6PA9 HSM‐I2‐5‐17 2/12/2013 0:00 PDB GW µg/L 6.1 = 0.5 U 0.81 = 20 = 0.5 UHSM‐I2‐5 I2 F6CA2 HSM‐I2‐5‐17 8/20/2012 9:01 PDB GW µg/L 5.7 = 1.0 U 0.65 LJ 32 = 1.0 UHSM‐I2‐5 I2 F5G82 HSM‐I2‐5‐17 2/27/2012 12:30 PDB GW µg/L 5 = 0.5 U 0.73 = 20 = 0.5 UHSM‐I2‐5 I2 F4EA4 HSM‐I2‐5‐I2‐17‐Q311 8/22/2011 8:15 PDB GW µg/L 6.9 = 5.0 U 1.1 LJ 31 = 2.0 UHSM‐I2‐5 I2 HSM‐I2‐5‐I2‐17‐Q111 HSM‐I2‐5‐I2‐17 2/14/2011 8:11 PDB GW µg/L 5.2 = 0.5 U 0.6 = 25.6 = 0.5 UHSM‐I2‐5 I2 F3LW0 HSM‐I2‐5‐17‐Q310 8/30/2010 13:05 PDB GW µg/L 5.3 = 0.5 U 1.3 = 21 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17_100201 HSM‐I2‐5‐17 2/1/2010 12:35 PDB GW µg/L 6 = 0.5 U 1.2 = 31.2 = 0.5 UHSM‐I2‐5 I2 F3B61 HSM‐I2‐5‐17 10/26/2009 9:47 PDB GW µg/L 5.4 = 0.5 U 1.1 = 29 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐FD‐Q209 HSM‐I2‐5‐17‐FD 4/20/2009 8:47 PDB GW µg/L 6.8 = 0.5 U 1.2 = 40.2 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐Q209 HSM‐I2‐5‐17 4/20/2009 8:46 PDB GW µg/L 6.8 = 0.5 U 1.2 = 42.7 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐Q408 HSM‐I2‐5‐17 10/6/2008 10:36 PDB GW µg/L 7.5 = 0.5 U 1.4 = 41.8 = 0.5 UHSM‐I2‐5 I2 F2RY7 HSM‐I2‐5‐17 4/14/2008 0:00 PDB GW µg/L 9.2 = 0.5 U 2 = 71 = 0.5 UHSM‐I2‐5 I2 HSM‐I2‐5‐17‐Q407 HSM‐I2‐5‐17 10/1/2007 8:20 PDB GW µg/L 10.2 = 0.5 U 2.4 = 58 = 0.5 UHSM‐I2‐5 I2 HSM‐12‐5_070219 HSM‐I2‐5‐17 2/19/2007 8:00 PDB GW µg/L 10.2 JL 0.5 UJ 2.3 JL 72.8 JL 0.5 UJHSM‐I2‐5 I2 F2642DL HSM‐I2‐5‐17 8/29/2006 7:40 PDB GW µg/L 51 =HSM‐I2‐5 I2 F2642 HSM‐I2‐5‐17 8/29/2006 7:40 PDB GW µg/L 7.2 J 0.5 U 1 J 0.5 UHSM‐I2‐5 I2 F1YR1DL HSM‐I2‐5‐17 2/6/2006 8:45 PDB GW µg/L 62 =HSM‐I2‐5 I2 F1YR1 HSM‐I2‐5‐17 2/6/2006 8:45 PDB GW µg/L 7.3 = 0.5 U 0.99 = 0.5 UHSM‐I2‐5 I2 F1YR0DL HSM‐I2‐5‐12 2/6/2006 8:43 PDB GW µg/L 36 =HSM‐I2‐5 I2 F1YR0 HSM‐I2‐5‐12 2/6/2006 8:43 PDB GW µg/L 7 J 0.5 U 1.1 = 0.5 UHSM‐I2‐5 I2 F1P16DL HSM‐I2‐5‐12 7/13/2005 8:38 PDB GW µg/L 74 =HSM‐I2‐5 I2 F1P16 HSM‐I2‐5‐12 7/13/2005 8:38 PDB GW µg/L 9.6 = 0.5 U 1.6 = 0.5 UHSM‐I2‐5 I2 F1P17DL HSM‐I2‐5‐17 7/13/2005 8:36 PDB GW µg/L 95 =HSM‐I2‐5 I2 F1P17 HSM‐I2‐5‐17 7/13/2005 8:36 PDB GW µg/L 13 = 0.5 U 1.9 = 0.5 UHSM‐I2‐5 I2 F1P15DL HSM‐I2‐5‐7 7/13/2005 8:32 PDB GW µg/L 61 =HSM‐I2‐5 I2 F1P15 HSM‐I2‐5‐7 7/13/2005 8:32 PDB GW µg/L 9.9 = 0.5 U 1.6 = 0.3 LJHSM‐I2‐5 I2 F1P14DL HSM‐I2‐5‐2 7/13/2005 8:29 PDB GW µg/L 34 =HSM‐I2‐5 I2 F1P14 HSM‐I2‐5‐2 7/13/2005 8:29 PDB GW µg/L 7.5 = 0.5 U 1.2 = 0.5 UHSM‐I2‐5 I2 F1D93DL HSM‐I2‐5 4/19/2005 9:30 LFS GW µg/L 59 =HSM‐I2‐5 I2 F1D93 HSM‐I2‐5 4/19/2005 9:30 LFS GW µg/L 11 = 0.5 U 1.6 = 0.26 LJHSM‐I2‐5 I2 F1DC1DL HSM‐I2‐5‐17 4/19/2005 8:38 PDB GW µg/L 99 =HSM‐I2‐5 I2 F1DC1 HSM‐I2‐5‐17 4/19/2005 8:38 PDB GW µg/L 16 = 0.5 U 2.1 = 0.36 LJHSM‐I2‐5 I2 F1DC0 HSM‐I2‐5‐12 4/19/2005 8:36 PDB GW µg/L 9.8 = 4.2 U 2 LJ 73 = 4.2 UHSM‐I2‐5 I2 F1DB9 HSM‐I2‐5‐7 4/19/2005 8:30 PDB GW µg/L 11 = 2.5 U 1.8 LJ 45 J 2.5 UHSM‐I2‐5 I2 F1DB8DL HSM‐I2‐5‐2 4/19/2005 8:27 PDB GW µg/L 65 =HSM‐I2‐5 I2 F1DB8 HSM‐I2‐5‐2 4/19/2005 8:27 PDB GW µg/L 11 = 0.5 U 1.6 = 0.25 LJHSM‐I2‐5 I2 F1808DL HSM‐I2‐5 11/15/2004 11:30 LFS GW µg/L 54 =HSM‐I2‐5 I2 F1808 HSM‐I2‐5 11/15/2004 11:30 LFS GW µg/L 9.6 = 0.5 U 1.6 = 0.5 UHSM‐I2‐5 I2 F1812DL HSM‐I2‐5‐17 11/15/2004 10:54 PDB GW µg/L 86 =HSM‐I2‐5 I2 F1812 HSM‐I2‐5‐17 11/15/2004 10:54 PDB GW µg/L 13 = 0.5 U 1.6 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 11 OF 64
011499
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodHSM‐I2‐5 I2 F1811DL HSM‐I2‐5‐12 11/15/2004 10:52 PDB GW µg/L 71 =HSM‐I2‐5 I2 F1811 HSM‐I2‐5‐12 11/15/2004 10:52 PDB GW µg/L 9.8 = 0.5 U 1.4 = 0.5 UHSM‐I2‐5 I2 F1810DL HSM‐I2‐5‐7 11/15/2004 10:50 PDB GW µg/L 69 =HSM‐I2‐5 I2 F1810 HSM‐I2‐5‐7 11/15/2004 10:50 PDB GW µg/L 9.9 = 0.5 U 1.4 = 0.5 UHSM‐I2‐5 I2 F1809DL HSM‐I2‐5‐2 11/15/2004 10:48 PDB GW µg/L 69 =HSM‐I2‐5 I2 F1809 HSM‐I2‐5‐2 11/15/2004 10:48 PDB GW µg/L 9.6 = 0.5 U 1.4 = 0.5 UHSM‐I2‐5 I2 F0NF9 HSM‐I2‐5‐104 12/3/2003 14:14 PDB GW µg/L 5 = 0.5 U 0.7 = 0.5 UHSM‐I2‐5 I2 F0NF9DL HSM‐I2‐5‐104 12/3/2003 14:14 PDB GW µg/L 29 =HSM‐I2‐5 I2 F0NF8 HSM‐I2‐5‐99 12/3/2003 14:10 PDB GW µg/L 3.8 = 0.5 U 0.53 = 23 = 0.5 UHSM‐I2‐5 I2 F0NF7 HSM‐I2‐5‐94 12/3/2003 14:08 PDB GW µg/L 4.7 = 0.5 U 0.71 = 0.5 UHSM‐I2‐5 I2 F0NF7DL HSM‐I2‐5‐94 12/3/2003 14:08 PDB GW µg/L 21 =HSM‐I2‐5 I2 F0NF6 HSM‐I2‐5‐89 12/3/2003 14:05 PDB GW µg/L 3.7 = 0.5 U 0.58 = 20 = 0.5 UHSM‐I2‐5 I2 HSMI25Q403 HSMI25Q403 11/13/2003 10:43 unknown GW µg/L 7.2 = 0.7936 < 45 = 0.2227 <
McDonalds (D2) NA 5/10/2020 0:00 unknownMcDonalds (D2) D2 McDonalds‐D2‐8‐022014 McDonalds‐D2‐2 2/17/2014 8:10 PDB GW µg/L 2.1 = 0.5 U 1.2 = 6.6 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐5‐022014 McDonalds‐D2‐5 2/17/2014 8:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.8 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐2‐022014 McDonalds‐D2‐8 2/17/2014 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.6 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐8‐0813 McDonalds‐D2‐8 8/12/2013 12:35 PDB WG µg/L 3 = 0.5 U 2.2 = 9.2 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐5‐0813 McDonalds‐D2‐5 8/12/2013 12:30 PDB WG µg/L 0.7 = 0.5 U 0.5 = 3.6 = 0.5 UMcDonalds (D2) D2 McDonalds‐D2‐2‐0813 McDonalds‐D2‐2 8/12/2013 12:25 PDB WG µg/L 0.9 = 0.5 U 0.5 U 6.6 = 0.5 UMcDonalds (D2) D2 F6PB1 McDonalds‐D2‐5 2/18/2013 0:00 PDB GW µg/L 3.3 = 0.26 LJ 2.3 = 10 = 0.5 UMcDonalds (D2) D2 F6PB0 McDonalds‐D2‐2 2/18/2013 0:00 PDB GW µg/L 0.74 = 0.5 U 0.41 LJ 3.9 = 0.5 UMcDonalds (D2) D2 F6PB2 McDonalds‐D2‐8 2/18/2013 0:00 PDB GW µg/L 3.8 = 0.5 U 4.7 = 6 = 0.5 UMcDonalds (D2) D2 F6CD5 McDonalds‐D2‐8 8/20/2012 12:40 PDB GW µg/L 3.4 = 0.16 LJ 2.5 = 8.7 = 0.5 UMcDonalds (D2) D2 F6CD4 McDonalds‐D2‐5 8/20/2012 12:38 PDB GW µg/L 0.71 = 0.040 LJ 0.38 LJ 3.3 = 0.5 UMcDonalds (D2) D2 F6CD3 McDonalds‐D2‐2 8/20/2012 12:37 PDB GW µg/L 1.6 = 0.041 LJ 0.80 = 11 = 0.5 UMcDonalds (D2) D2 F5G07 McDonalds‐D2‐2 2/27/2012 13:33 PDB GW µg/L 0.45 LJ 0.5 U 0.14 LJ 3.3 = 0.5 UMcDonalds (D2) D2 F5G08 McDonalds‐D2‐5 2/27/2012 13:30 PDB GW µg/L 1.9 = 0.5 U 0.82 = 8 = 0.5 UMcDonalds (D2) D2 F5G09 McDonalds‐D2‐8 2/27/2012 13:28 PDB GW µg/L 2.4 = 0.5 U 2.3 = 5.8 = 0.5 UMcDonalds (D2) D2 F4EA7 Mcdonalds‐D2‐12‐Q311 8/22/2011 13:40 PDB GW µg/L 2.8 LJ 5.0 U 1.1 LJ 11 = 2.0 UMcDonalds (D2) D2 F4EA6 Mcdonalds‐D2‐7‐Q311 8/22/2011 13:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 3.5 LJ 2.0 UMcDonalds (D2) D2 F4EA5 Mcdonalds‐D2‐2‐Q311 8/22/2011 13:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 4.7 LJ 2.0 UMcDonalds (D2) D2 F3S11 McDonalds‐D2‐12 2/15/2011 11:55 PDB GW µg/L 0.3 LJ 0.5 U 0.5 U 0.74 = 0.5 UMcDonalds (D2) D2 F3S10 McDonalds‐D2‐12 2/15/2011 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMcDonalds (D2) D2 F3S09 McDonalds‐D2‐7 2/15/2011 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMcDonalds (D2) D2 F3S08 McDonalds‐D2‐2 2/15/2011 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMcDonalds (D2) D2 FGS98 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 0.5 LJ 1 U 1 U 1 = 1 UMcDonalds (D2) D2 FW547 NA 2/8/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
MNW‐01 (I2) NA 5/10/2020 0:00 unknownMNW‐01 (I2) I2 MNW‐1‐I2‐7‐022014‐FD MNW‐1‐I2‐7 2/17/2014 9:20 PDB GW µg/L 3.8 = 0.5 U 0.9 = 17.8 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐022014 MNW‐1‐I2‐7 2/17/2014 8:20 PDB GW µg/L 4.1 = 0.5 U 1 = 19 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐0813 MNW‐1‐I2‐7 8/13/2013 9:00 PDB WG µg/L 3.7 = 0.5 U 0.6 = 22.4 = 0.5 UMNW‐01 (I2) I2 F6PF0 MNW‐1‐I2‐7 2/18/2013 0:00 PDB GW µg/L 2.7 = 0.5 U 0.22 LJ 13 = 0.5 UMNW‐01 (I2) I2 F6CA3 MNW‐1‐I2‐7 8/20/2012 9:38 PDB GW µg/L 3.4 = 1.0 U 0.29 LJ 17 = 1.0 UMNW‐01 (I2) I2 F5G86 MNW‐1‐I2‐7 2/28/2012 8:20 PDB GW µg/L 2.6 = 0.5 U 0.5 U 14 = 0.5 UMNW‐01 (I2) I2 F4EC4 MNW‐1‐I2‐7‐FD‐Q311 8/23/2011 7:59 PDB GW µg/L 3.5 LJ 5.0 U 5.0 U 18 = 2.0 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 12 OF 64
011500
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐01 (I2) I2 F4EC3 MNW‐1‐I2‐7‐Q311 8/23/2011 7:57 PDB GW µg/L 2.9 LJ 5.0 U 5.0 U 15 = 2.0 UMNW‐01 (I2) I2 MNW‐1‐I2‐5‐Q111 MNW‐1‐I2‐7 2/16/2011 8:25 PDB GW µg/L 1.9 = 0.5 U 0.5 U 10.7 JH 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q310‐FD MNW‐1‐I2‐7‐Q310‐FD 9/8/2010 8:30 PDB GW µg/L 2.1 = 0.5 U 0.5 U 9.2 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q310 MNW‐1‐I2‐7‐Q310 9/8/2010 8:25 PDB GW µg/L 2.0 = 0.5 U 0.5 U 10.2 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7_100201 MNW‐1‐I2‐7 2/1/2010 7:45 PDB GW µg/L 1.9 = 0.5 U 0.5 U 8.4 = 0.5 UMNW‐01 (I2) I2 F3B18 MNW‐1‐I2‐7 10/26/2009 9:02 PDB GW µg/L 1.7 = 0.5 U 0.5 U 8.4 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q209 MNW‐1‐I2‐7 4/20/2009 8:02 PDB GW µg/L 2.3 = 0.5 U 0.5 U 12.7 = 0.5 UMNW‐01 (I2) I2 MNW‐1‐I2‐7‐Q408 MNW‐1‐I2‐7 10/6/2008 8:10 PDB GW µg/L 2.4 = 0.5 U 0.5 U 12.8 = 0.5 UMNW‐01 (I2) I2 F2643 MNW‐1‐I2‐7 8/29/2006 7:20 PDB GW µg/L 0.97 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐01 (I2) I2 F1NN6 MNW‐1‐I2‐17 7/12/2005 10:51 PDB GW µg/L 1.2 = 0.5 U 0.5 U 2.2 = 0.5 UMNW‐01 (I2) I2 F1NN5 MNW‐1‐I2‐12 7/12/2005 10:49 PDB GW µg/L 1.3 = 0.5 U 0.17 LJ 2.3 = 0.1 LJMNW‐01 (I2) I2 F1NN3 MNW‐1‐I2‐7 7/12/2005 10:48 PDB GW µg/L 0.9 = 0.5 U 0.19 LJ 2.7 = 0.5 UMNW‐01 (I2) I2 F1NN2 MNW‐1‐I2‐2 7/12/2005 10:47 PDB GW µg/L 0.86 = 0.5 U 0.19 LJ 2.7 = 0.5 UMNW‐01 (I2) I2 F1DJ7 MNW‐1‐I2‐17 4/20/2005 8:41 PDB GW µg/L 0.81 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐01 (I2) I2 F1DJ6 MNW‐1‐I2‐12 4/20/2005 8:38 PDB GW µg/L 0.74 = 0.5 U 0.5 U 1.5 = 0.5 UMNW‐01 (I2) I2 F1DJ4 MNW‐1‐I2‐7 4/20/2005 8:33 PDB GW µg/L 0.75 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐01 (I2) I2 F1DJ3 MNW‐1‐I2‐2 4/20/2005 8:29 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐01 (I2) I2 F17G9 MNW‐1‐I2‐17 11/9/2004 8:40 PDB GW µg/L 1.9 = 0.5 U 0.5 U 2.6 = 0.25 LJMNW‐01 (I2) I2 F17G8 MNW‐1‐I2‐12 11/9/2004 8:33 PDB GW µg/L 2 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐01 (I2) I2 F17G7 MNW‐1‐I2‐7 11/9/2004 8:26 PDB GW µg/L 1.7 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐01 (I2) I2 F17G6 MNW‐1‐I2‐2 11/9/2004 8:18 PDB GW µg/L 1.7 = 0.5 U 0.5 U 2.1 = 0.5 UMNW‐01 (I2) I2 MNW1Q403 MNW1Q403 11/16/2003 11:35 unknown GW µg/L 3.9 = 0.7936 < 10 = 0.4 J
MNW‐02 (I2) 5/10/2020 0:00 unknownMNW‐02 (I2) I2 F6PF1 MNW‐2‐I2‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F3S45 MNW‐2‐I2‐5 2/15/2011 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 MNW‐2‐I2‐7‐Q209 MNW‐2‐I2‐7 4/20/2009 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 MNW‐2‐I2‐7‐Q407 MNW‐2‐I2‐7 10/2/2007 8:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1P00 MNW‐2‐I2‐17 7/13/2005 8:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1NZ9 MNW‐2‐I2‐12 7/13/2005 8:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1NZ8 MNW‐2‐I2‐7 7/13/2005 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1NZ7 MNW‐2‐I2‐2 7/13/2005 8:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT3 MNW‐2‐I2‐17 4/20/2005 13:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT2 MNW‐2‐I2‐12 4/20/2005 13:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT1 MNW‐2‐I2‐7 4/20/2005 13:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F1DT0 MNW‐2‐I2‐2 4/20/2005 13:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17D3 MNW‐2‐I2 11/17/2004 8:40 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17J0 MNW‐2‐I2‐17 11/8/2004 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17H9 MNW‐2‐I2‐12 11/8/2004 11:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17H8 MNW‐2‐I2‐7 11/8/2004 11:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 F17H7 MNW‐2‐I2‐2 11/8/2004 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐02 (I2) I2 MNW2Q403 MNW2Q403 11/15/2003 11:42 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐03 (D1) 5/10/2020 0:00 unknownMNW‐03 (D1) D1 F6PF2 MNW‐3‐D1‐7 2/18/2013 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F3S19 MNW‐3‐D1‐5 2/15/2011 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 MNW‐3‐D1‐7‐Q209 MNW‐3‐D1‐7 4/21/2009 14:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐03 (D1) D1 MNW‐3‐D1‐7‐Q407 MNW‐3‐D1‐7 10/2/2007 8:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 13 OF 64
011501
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐03 (D1) D1 F1P04 MNW‐3‐D1‐17 7/12/2005 11:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1P03 MNW‐3‐D1‐12 7/12/2005 11:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1P02 MNW‐3‐D1‐7 7/12/2005 11:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1P01 MNW‐3‐D1‐2 7/12/2005 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT7 MNW‐3‐D1‐17 4/20/2005 14:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT6 MNW‐3‐D1‐12 4/20/2005 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT5 MNW‐3‐D1‐7 4/20/2005 13:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F1DT4 MNW‐3‐D1‐2 4/20/2005 13:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17N1 MNW‐3‐D1‐17 11/8/2004 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17M9 MNW‐3‐D1‐12 11/8/2004 10:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17M8 MNW‐3‐D1‐7 11/8/2004 10:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 F17M7 MNW‐3‐D1‐2 11/8/2004 9:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D1) D1 MNW3D1Q403 MNW3D1Q403 11/18/2003 14:52 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐03 (D2) 5/10/2020 0:00 unknownMNW‐03 (D2) D2 F6PF3 MNW‐3‐D2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJvMNW‐03 (D2) D2 F3S21 MNW‐3‐D2‐5 2/15/2011 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐03 (D2) D2 F3S20 MNW‐3‐D2‐5 2/15/2011 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐03 (D2) D2 MNW‐3‐D2‐7‐Q209 MNW‐3‐D2‐7 4/21/2009 14:05 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐03 (D2) D2 MNW‐3‐D2‐7‐Q407 MNW‐3‐D2‐7 10/2/2007 8:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P08 MNW‐3‐D2‐17 7/12/2005 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P07 MNW‐3‐D2‐12 7/12/2005 11:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P06 MNW‐3‐D2‐7 7/12/2005 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1P05 MNW‐3‐D2‐2 7/12/2005 10:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DW1 MNW‐3‐D2‐17 4/20/2005 14:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DW0 MNW‐3‐D2‐12 4/20/2005 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DT9 MNW‐3‐D2‐7 4/20/2005 14:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F1DT8 MNW‐3‐D2‐2 4/20/2005 14:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17D4 MNW‐3‐D2 11/8/2004 11:54 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N2 MNW‐3‐D2‐2 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N3 MNW‐3‐D2‐7 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N4 MNW‐3‐D2‐12 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 F17N5 MNW‐3‐D2‐17 11/8/2004 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D2) D2 MNW3D2Q403 MNW3D2Q403 11/19/2003 9:35 unknown GW µg/L 0.2937 <
MNW‐03 (D3) 5/10/2020 0:00 unknownMNW‐03 (D3) D3 F6PF4 MNW‐3‐D3‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F3S22 MNW‐3‐D3‐5 2/15/2011 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.31 LJ 0.5 UMNW‐03 (D3) D3 MNW‐3‐D3‐7‐Q209 MNW‐3‐D3‐7 4/21/2009 14:15 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐03 (D3) D3 MNW‐3‐D3‐7‐Q407 MNW‐3‐D3‐7 10/2/2007 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P13 MNW‐3‐D3‐17 7/12/2005 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P12 MNW‐3‐D3‐12 7/12/2005 10:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P11 MNW‐3‐D3‐7 7/12/2005 10:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1P09 MNW‐3‐D3‐2 7/12/2005 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW6 MNW‐3‐D3‐17 4/20/2005 14:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW5 MNW‐3‐D3‐12 4/20/2005 14:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW4 MNW‐3‐D3‐7 4/20/2005 14:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F1DW2 MNW‐3‐D3‐2 4/20/2005 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 14 OF 64
011502
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐03 (D3) D3 F17P0 MNW‐3‐D3‐17 11/8/2004 10:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.22 LJMNW‐03 (D3) D3 F17N9 MNW‐3‐D3‐12 11/8/2004 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F17N8 MNW‐3‐D3‐7 11/8/2004 10:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 F17N6 MNW‐3‐D3‐2 11/8/2004 10:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐03 (D3) D3 MNW3D3Q403 MNW3D3Q403 11/19/2003 16:12 unknown GW µg/L 0.2937 <
MNW‐04 (D1) 5/10/2020 0:00 unknownMNW‐04 (D1) D1 MNW‐4‐D1‐12‐022014 MNW‐4‐D1‐12 2/18/2014 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F6PF5 MNW‐4‐D1‐12 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.3 LJ 0.5 UMNW‐04 (D1) D1 F5G31 MNW‐4‐D1‐12 2/28/2012 13:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F3S23 MNW‐4‐D1‐12 2/15/2011 7:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.35 LJ 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12_100201‐FD MNW‐4‐D1‐12 2/1/2010 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12_100201 MNW‐4‐D1‐12 2/1/2010 8:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12‐Q209 MNW‐4‐D1‐12 4/20/2009 12:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12‐Q408 MNW‐4‐D1‐12 10/6/2008 12:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F2RQ1 MNW‐4‐D1‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1‐12‐Q407 MNW‐4‐D1‐12 10/2/2007 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW‐4‐D1_070219 MNW‐4‐D1‐12 2/19/2007 8:05 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐04 (D1) D1 F2675 MNW‐4‐D1‐12 8/28/2006 13:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1YR4 MNW‐4‐D1‐12 2/6/2006 8:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1P73 MNW‐4‐D1‐17 7/12/2005 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UMNW‐04 (D1) D1 F1P72 MNW‐4‐D1‐12 7/12/2005 10:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 UMNW‐04 (D1) D1 F1P71 MNW‐4‐D1‐7 7/12/2005 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.17 LJ 0.5 UMNW‐04 (D1) D1 F1P70 MNW‐4‐D1‐2 7/12/2005 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1E21 MNW‐4‐D1‐17 4/18/2005 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.1 LJ 0.5 UMNW‐04 (D1) D1 F1E20 MNW‐4‐D1‐12 4/18/2005 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.11 LJ 0.5 UMNW‐04 (D1) D1 F1E19 MNW‐4‐D1‐7 4/18/2005 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F1E18 MNW‐4‐D1‐2 4/18/2005 10:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P4 MNW‐4‐D1‐17 11/8/2004 12:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P3 MNW‐4‐D1‐12 11/8/2004 12:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P2 MNW‐4‐D1‐7 11/8/2004 12:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 F17P1 MNW‐4‐D1‐2 11/8/2004 12:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D1) D1 MNW4D1Q403 MNW4D1Q403 12/5/2003 9:32 unknown GW µg/L 0.7 J 1.1 = 2.4 = 0.2227 <
MNW‐04 (D2) 5/10/2020 0:00 unknownMNW‐04 (D2) D2 MNW‐4‐D2‐7‐022014 MNW‐4‐D2‐7 2/18/2014 9:47 PDB GW µg/L 2.8 = 0.5 U 0.6 = 2.6 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐0813 MNW‐4‐D2‐7 8/12/2013 10:55 PDB WG µg/L 2.3 = 0.5 U 0.5 U 2.3 = 0.5 UMNW‐04 (D2) D2 F6PF6 MNW‐4‐D2‐7 2/13/2013 0:00 PDB GW µg/L 2.3 = 0.5 U 0.37 LJ 2.1 = 0.5 UMNW‐04 (D2) D2 F5G32 MNW‐4‐D2‐7 2/28/2012 13:15 PDB GW µg/L 0.96 UM 0.5 U 0.19 LJ 1.4 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q111 MNW‐4‐D2‐7 3/24/2011 10:20 PDB GW µg/L 0.5 = 0.5 U 0.5 U 1.2 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7_100201‐FD MNW‐4‐D2‐7 2/1/2010 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.9 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7_100201 MNW‐4‐D2‐7 2/1/2010 9:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐FD‐Q209 MNW‐4‐D2‐7‐FD 4/20/2009 13:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q209 MNW‐4‐D2‐7 4/20/2009 13:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q408 MNW‐4‐D2‐7 10/6/2008 12:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F2RQ2 MNW‐4‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.59 = 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2‐7‐Q407 MNW‐4‐D2‐7 10/2/2007 10:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 MNW‐4‐D2_070219 MNW‐4‐D2‐7 2/19/2007 8:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 15 OF 64
011503
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐04 (D2) D2 F2676 MNW‐4‐D2‐7 8/28/2006 13:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F1YR5 MNW‐4‐D2‐7 2/6/2006 8:36 PDB GW µg/L 4.9 = 0.5 U 1.3 = 13 = 0.5 UMNW‐04 (D2) D2 F1P78 MNW‐4‐D2‐17 7/12/2005 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UMNW‐04 (D2) D2 F1P77 MNW‐4‐D2‐12 7/12/2005 10:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F1P76 MNW‐4‐D2‐7 7/12/2005 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UMNW‐04 (D2) D2 F1P75 MNW‐4‐D2‐2 7/12/2005 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.21 LJ 0.5 UMNW‐04 (D2) D2 F1E26 MNW‐4‐D2‐17 4/18/2005 11:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UMNW‐04 (D2) D2 F1E25 MNW‐4‐D2‐12 4/18/2005 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.24 LJ 0.5 UMNW‐04 (D2) D2 F1E24 MNW‐4‐D2‐7 4/18/2005 11:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.21 LJ 0.5 UMNW‐04 (D2) D2 F1E23 MNW‐4‐D2‐2 4/18/2005 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.17 LJ 0.5 UMNW‐04 (D2) D2 F17D5 MNW‐4‐D2 11/16/2004 12:15 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.35 LJ 0.5 UMNW‐04 (D2) D2 F17P9 MNW‐4‐D2‐17 11/8/2004 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F17P8 MNW‐4‐D2‐12 11/8/2004 14:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F17P7 MNW‐4‐D2‐7 11/8/2004 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 F17P6 MNW‐4‐D2‐2 11/8/2004 13:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D2) D2 MNW4D2Q403 MNW4D2Q403 12/6/2003 11:33 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐04 (D3) 5/10/2020 0:00 unknownMNW‐04 (D3) D3 MNW‐4‐D3‐7‐022014 MNW‐4‐D3‐7 2/18/2014 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F6PF7 MNW‐4‐D3‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F5G33 MNW‐4‐D3‐7 2/28/2012 12:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F3S25 MNW‐4‐D3‐7 2/15/2011 8:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7_100201 MNW‐4‐D3‐7 2/1/2010 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7‐Q209 MNW‐4‐D3‐7 4/20/2009 12:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7‐Q408 MNW‐4‐D3‐7 10/6/2008 13:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F2RQ3 MNW‐4‐D3‐7 4/14/2008 0:00 PDB GW µg/L 6.9 = 0.29 LJ 3.1 = 9 = 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3‐7‐Q407 MNW‐4‐D3‐7 10/2/2007 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW‐4‐D3_070219 MNW‐4‐D3‐7 2/19/2007 8:38 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐04 (D3) D3 F2677 MNW‐4‐D3‐7 8/28/2006 13:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1YR7 MNW‐4‐D3‐17 2/6/2006 8:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1YR6 MNW‐4‐D3‐7 2/6/2006 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P82 MNW‐4‐D3‐17 7/12/2005 11:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P81 MNW‐4‐D3‐12 7/12/2005 11:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P80 MNW‐4‐D3‐7 7/12/2005 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1P79 MNW‐4‐D3‐2 7/12/2005 11:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E30 MNW‐4‐D3‐17 4/18/2005 12:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E29 MNW‐4‐D3‐12 4/18/2005 12:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E28 MNW‐4‐D3‐7 4/18/2005 12:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F1E27 MNW‐4‐D3‐2 4/18/2005 12:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐04 (D3) D3 F17Q3 MNW‐4‐D3‐17 11/8/2004 13:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F17Q2 MNW‐4‐D3‐12 11/8/2004 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 F17Q1 MNW‐4‐D3‐7 11/8/2004 13:15 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐04 (D3) D3 F17Q0 MNW‐4‐D3‐2 11/8/2004 13:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐04 (D3) D3 MNW4D3Q403 MNW4D3Q403 12/3/2003 11:50 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐05 (D1) 5/10/2020 0:00 unknownMNW‐05 (D1) D1 MNW‐5‐D1‐12‐022014 MNW‐5‐D1‐12 2/18/2014 12:07 PDB GW µg/L 3.6 = 0.5 U 1.6 = 4.4 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐022014 MNW‐5‐D1‐7 2/18/2014 12:05 PDB GW µg/L 5.6 = 1.2 = 2.2 = 8.9 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 16 OF 64
011504
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐05 (D1) D1 MNW‐5‐D1‐12‐0813 MNW‐5‐D1‐12 8/13/2013 9:10 PDB WG µg/L 3.9 = 0.5 U 2.1 = 5.2 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐0813FD MNW‐5‐D1‐7 8/13/2013 9:05 PDB WG µg/L 5.4 = 1.2 = 1.9 = 7.8 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐0813 MNW‐5‐D1‐7 8/13/2013 9:00 PDB WG µg/L 5.4 = 1.4 = 2.3 = 9 = 0.5 UMNW‐05 (D1) D1 F6PF9 MNW‐5‐D1‐12‐FD 2/13/2013 0:00 PDB GW µg/L 4.2 = 0.18 LJ 1.6 = 4.8 = 0.5 UMNW‐05 (D1) D1 F6PF8 MNW‐5‐D1‐12 2/13/2013 0:00 PDB GW µg/L 4.1 = 0.19 LJ 1.6 = 4.9 = 0.5 UMNW‐05 (D1) D1 F6PG0 MNW‐5‐D1‐7 2/13/2013 0:00 PDB GW µg/L 5.8 = 1.1 = 2.1 = 8.4 = 0.5 UMNW‐05 (D1) D1 F6CD6 MNW‐5‐D1‐12 8/20/2012 12:03 PDB GW µg/L 3.6 = 0.16 LJ 1.4 = 4.6 = 0.5 UMNW‐05 (D1) D1 F6CD7 MNW‐5‐D1‐7 8/20/2012 12:02 PDB GW µg/L 5.2 = 0.87 = 1.7 = 7.7 = 0.5 UMNW‐05 (D1) D1 F5G34 MNW‐5‐D1‐12 2/28/2012 10:29 PDB GW µg/L 2.9 = 0.5 U 1.3 = 4.3 = 0.5 UMNW‐05 (D1) D1 F5G35 MNW‐5‐D1‐7 2/28/2012 10:27 PDB GW µg/L 4 = 0.69 = 1.4 = 6.9 = 0.5 UMNW‐05 (D1) D1 F4EC5 MNW‐5‐D1‐12‐Q311 8/22/2011 11:22 PDB GW µg/L 4.6 LJ 5.0 U 2.2 LJ 6.1 = 2.0 UMNW‐05 (D1) D1 F4EC6 MNW‐5‐D1‐7‐Q311 8/22/2011 11:20 PDB GW µg/L 5.3 = 5.0 U 2.0 LJ 8.4 = 2.0 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q111 MNW‐5‐D1‐12 2/14/2011 9:07 PDB GW µg/L 2.7 = 0.5 U 1.5 = 3.8 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q111 MNW‐5‐D1‐7 2/14/2011 9:06 PDB GW µg/L 3.6 = 0.5 U 1.6 = 5.2 = 0.5 UMNW‐05 (D1) D1 F3LQ4 MNW‐5‐D1‐12‐Q310 9/2/2010 9:00 PDB GW µg/L 2.7 = 0.5 U 1.5 = 3.8 = 0.5 UMNW‐05 (D1) D1 F3LQ3 MNW‐5‐D1‐7‐Q310 9/2/2010 8:55 PDB GW µg/L 2.9 = 0.5 U 1.5 = 4.1 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12_100201 MNW‐5‐D1‐12 2/1/2010 13:17 PDB GW µg/L 3.5 = 0.5 U 1.8 = 4.9 = 0.5 UMNW‐05 (D1) D1 F3B19 MNW‐5‐D1‐7 10/27/2009 8:10 PDB GW µg/L 4.1 = 0.5 U 1.8 = 4.9 = 0.5 UMNW‐05 (D1) D1 F3B20 MNW‐5‐D1‐12 10/27/2009 8:06 PDB GW µg/L 4.2 = 0.5 U 2 = 5.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q209 MNW‐5‐D1‐7 4/20/2009 9:14 PDB GW µg/L 4.6 = 0.5 = 2.0 = 7.2 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q209 MNW‐5‐D1‐12 4/20/2009 9:03 PDB GW µg/L 4.4 = 0.5 U 2.0 = 6.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q408 MNW‐5‐D1‐12 10/7/2008 9:06 PDB GW µg/L 5 = 0.5 U 2.4 = 7.0 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q408 MNW‐5‐D1‐7 10/7/2008 9:02 PDB GW µg/L 5 = 0.5 U 2.3 = 6.8 = 0.5 UMNW‐05 (D1) D1 F2RQ5 MNW‐5‐D1‐12 4/14/2008 0:00 PDB GW µg/L 12 = 0.71 = 4.9 = 19 = 0.5 UMNW‐05 (D1) D1 F2RQ4 MNW‐5‐D1‐7 4/14/2008 0:00 PDB GW µg/L 5.8 = 0.5 U 2.6 = 7.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐7‐Q407 MNW‐5‐D1‐7 10/1/2007 10:40 PDB GW µg/L 5.8 = 0.5 U 2.7 = 7.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12‐Q407 MNW‐5‐D1‐12 10/1/2007 10:33 PDB GW µg/L 5.5 = 0.5 U 2.4 = 7.5 = 0.5 UMNW‐05 (D1) D1 MNW‐5‐D1‐12_070219 MNW‐5‐D1‐12 2/19/2007 9:19 PDB GW µg/L 5.6 JL 0.5 UJ 2.7 JL 9.0 JL 0.5 UJMNW‐05 (D1) D1 MNW‐5‐D1‐7_070219 MNW‐5‐D1‐7 2/19/2007 9:14 PDB GW µg/L 6 JL 0.5 UJ 2.9 JL 9.7 JL 0.5 UJMNW‐05 (D1) D1 F2678 MNW‐5‐D1‐12 8/28/2006 10:20 PDB GW µg/L 5.2 = 0.5 U 2.1 = 7.3 = 0.5 UMNW‐05 (D1) D1 F2679 MNW‐5‐D1‐7 8/28/2006 10:10 PDB GW µg/L 5.2 = 0.5 U 2 = 7.5 = 0.5 UMNW‐05 (D1) D1 F1YT7 MNW‐5‐D1‐12 2/6/2006 10:23 PDB GW µg/L 6.7 = 0.5 U 2.8 = 9.2 = 0.5 UMNW‐05 (D1) D1 F1YT6 MNW‐5‐D1‐7 2/6/2006 10:20 PDB GW µg/L 6.3 = 0.61 = 2.5 = 8.6 = 0.5 UMNW‐05 (D1) D1 F1P39 MNW‐5‐D1‐17 7/11/2005 11:21 PDB GW µg/L 8.2 = 0.4 LJ 3.6 = 11 J 0.2 LJMNW‐05 (D1) D1 F1P38 MNW‐5‐D1‐12 7/11/2005 11:20 PDB GW µg/L 8.3 = 0.43 LJ 3.7 = 11 = 0.2 LJMNW‐05 (D1) D1 F1P36 MNW‐5‐D1‐7 7/11/2005 11:15 PDB GW µg/L 7.2 = 0.39 LJ 3.1 = 10 = 0.18 LJMNW‐05 (D1) D1 F1P35 MNW‐5‐D1‐2 7/11/2005 11:14 PDB GW µg/L 7.5 = 0.59 = 3.4 = 11 = 0.5 UMNW‐05 (D1) D1 F1DY7 MNW‐5‐D1‐17 4/18/2005 12:06 PDB GW µg/L 8.8 = 0.58 = 3.2 = 11 J 0.5 UMNW‐05 (D1) D1 F1DY6 MNW‐5‐D1‐12 4/18/2005 12:04 PDB GW µg/L 10 = 0.6 = 3.8 = 12 = 0.5 UMNW‐05 (D1) D1 F1DY4 MNW‐5‐D1‐7 4/18/2005 12:00 PDB GW µg/L 9.4 = 0.79 = 3.3 = 11 = 0.5 UMNW‐05 (D1) D1 F1DY3 MNW‐5‐D1‐2 4/18/2005 11:58 PDB GW µg/L 5.9 = 1.1 = 2.1 = 8.1 = 0.5 UMNW‐05 (D1) D1 F1D99 MNW‐5‐D1 4/18/2005 11:00 LFS GW µg/L 5.7 = 0.77 = 2.2 = 9.3 J 0.15 LJMNW‐05 (D1) D1 F17Q7 MNW‐5‐D1‐17 11/9/2004 11:00 PDB GW µg/L 7.5 = 0.3 LJv 3.2 = 10 Jv 0.21 LJMNW‐05 (D1) D1 F17Q5 MNW‐5‐D1‐7 11/9/2004 10:50 PDB GW µg/L 15 J^ 0.81 J 6 J^ 18 J 0.5 UJvMNW‐05 (D1) D1 F17Q4 MNW‐5‐D1‐2 11/9/2004 10:45 PDB GW µg/L 7.4 J 0.88 J 2.9 J 9.4 J 0.5 UJvMNW‐05 (D1) D1 MNW5D1Q403 MNW5D1Q403 11/24/2003 17:08 unknown GW µg/L 4.6 = 1.2 = 6.1 = 0.2227 <
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 17 OF 64
011505
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐05 (D2) 5/10/2020 0:00 unknown
MNW‐05 (D2) D2 MNW‐5‐D2‐7‐022014 MNW‐5‐D2‐7 2/18/2014 11:48 PDB GW µg/L 9.5 = 0.8 = 4.2 = 15.4 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐0813 MNW‐5‐D2‐7 8/13/2013 9:30 PDB WG µg/L 8.6 = 1 = 3.6 = 16.4 = 0.5 UMNW‐05 (D2) D2 F6PG1 MNW‐5‐D2‐7 2/13/2013 0:00 PDB GW µg/L 8 = 0.47 LJ 3.1 = 12 = 0.5 UMNW‐05 (D2) D2 F6CD9 MNW‐5‐D2‐7‐FD 8/20/2012 11:52 PDB GW µg/L 8.0 = 0.40 LJ 2.8 = 13 = 0.5 UMNW‐05 (D2) D2 F6CD8 MNW‐5‐D2‐7 8/20/2012 11:50 PDB GW µg/L 8.2 = 0.44 LJ 2.8 = 14 = 0.5 UMNW‐05 (D2) D2 F5G36 MNW‐5‐D2‐7 2/28/2012 11:09 PDB GW µg/L 5.5 = 0.28 LJ 2.3 = 9.1 = 0.5 UMNW‐05 (D2) D2 F4EC7 MNW‐5‐D2‐7‐Q311 8/22/2011 11:23 PDB GW µg/L 12 = 5.0 U 4.7 LJ 19 = 2.0 UMNW‐05 (D2) D2 MNW‐5‐D2‐5‐Q111 MNW‐5‐D2‐7 2/14/2011 9:17 PDB GW µg/L 5.3 = 0.5 U 1.7 = 8.6 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q310 MNW‐5‐D2‐7‐Q310 9/8/2010 12:45 PDB GW µg/L 7.2 = 0.5 = 2.5 = 10.5 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7_100201 MNW‐5‐D2‐7 2/1/2010 13:26 PDB GW µg/L 7 = 0.6 = 3.2 = 11.1 = 0.5 UMNW‐05 (D2) D2 F3B21 MNW‐5‐D2‐7 10/26/2009 14:52 PDB GW µg/L 8.2 = 0.67 = 3.4 = 13 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐FD‐Q209 MNW‐5‐D2‐7‐FD 4/20/2009 9:33 PDB GW µg/L 7.4 = 0.6 = 3.3 = 13.1 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q209 MNW‐5‐D2‐7 4/20/2009 9:32 PDB GW µg/L 7.0 = 0.6 = 3.2 = 12.9 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q408 MNW‐5‐D2‐7 10/7/2008 9:39 PDB GW µg/L 9.8 = 0.5 = 3.9 = 15.1 = 0.5 UMNW‐05 (D2) D2 F2RQ6 MNW‐5‐D2‐7 4/14/2008 0:00 PDB GW µg/L 8.9 = 0.81 = 3.5 = 14 = 0.5 UMNW‐05 (D2) D2 F2RQ8 MNW‐5‐D2‐12 4/14/2008 0:00 PDB GW µg/L 8.5 = 0.86 = 3.4 = 15 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐7‐Q407 MNW‐5‐D2‐7 10/1/2007 11:25 PDB GW µg/L 10 = 0.6 = 4.3 = 17.3 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐12‐Q407 MNW‐5‐D2‐12 10/1/2007 11:20 PDB GW µg/L 8.2 = 0.7 = 3.4 = 14.6 = 0.5 UMNW‐05 (D2) D2 MNW‐5‐D2‐12_070219 MNW‐5‐D2‐12 2/19/2007 9:39 PDB GW µg/L 7.5 JL 0.8 JL 3.3 JL 15.4 JL 0.5 UJMNW‐05 (D2) D2 MNW‐5‐D2‐7_070219 MNW‐5‐D2‐7 2/19/2007 9:32 PDB GW µg/L 9.5 JL 0.8 JL 4.2 JL 18.6 JL 0.5 UJMNW‐05 (D2) D2 F2680 MNW‐5‐D2‐12 8/28/2006 10:50 PDB GW µg/L 6.2 = 0.74 = 2.1 = 12 = 0.5 UMNW‐05 (D2) D2 F2681 MNW‐5‐D2‐7 8/28/2006 10:35 PDB GW µg/L 7.6 = 0.65 = 2.7 = 14 = 0.5 UMNW‐05 (D2) D2 F1YW0 MNW‐5‐D2‐12 2/6/2006 10:43 PDB GW µg/L 4.7 = 0.71 = 1.8 = 8.4 = 0.5 UMNW‐05 (D2) D2 F1YT8 MNW‐5‐D2‐7 2/6/2006 10:40 PDB GW µg/L 7.6 = 0.85 = 2.9 = 14 = 0.5 UMNW‐05 (D2) D2 F1P43 MNW‐5‐D2‐17 7/11/2005 13:31 PDB GW µg/L 5.2 = 0.78 = 1.8 = 7.9 = 0.12 LJMNW‐05 (D2) D2 F1P42 MNW‐5‐D2‐12 7/11/2005 13:28 PDB GW µg/L 6.4 = 0.77 = 2.3 = 9.4 = 0.11 LJMNW‐05 (D2) D2 F1P41 MNW‐5‐D2‐7 7/11/2005 13:27 PDB GW µg/L 9.2 = 0.92 = 3.5 = 14 = 0.15 LJMNW‐05 (D2) D2 F1P40 MNW‐5‐D2‐2 7/11/2005 13:25 PDB GW µg/L 9.3 = 0.98 = 3.6 = 15 = 0.5 UMNW‐05 (D2) D2 F1DZ1 MNW‐5‐D2‐17 4/18/2005 13:44 PDB GW µg/L 5.1 = 0.86 = 1.7 = 8.3 = 0.5 UMNW‐05 (D2) D2 F1DZ0 MNW‐5‐D2‐12 4/18/2005 13:42 PDB GW µg/L 7.3 = 1.3 = 2.6 = 12 = 0.5 UMNW‐05 (D2) D2 F1DY9 MNW‐5‐D2‐7 4/18/2005 13:40 PDB GW µg/L 8.7 = 0.91 = 2.8 = 13 = 0.5 UMNW‐05 (D2) D2 F1DY8 MNW‐5‐D2‐2 4/18/2005 13:38 PDB GW µg/L 9.2 = 1.4 = 3.4 = 15 = 0.5 UMNW‐05 (D2) D2 F17R1 MNW‐5‐D2‐17 11/9/2004 11:40 PDB GW µg/L 6.7 = 0.68 = 2.3 = 12 = 0.5 UMNW‐05 (D2) D2 F17Q9 MNW‐5‐D2‐7 11/9/2004 11:30 PDB GW µg/L 12 = 1.2 = 3.9 = 22 = 0.5 UMNW‐05 (D2) D2 F17Q8 MNW‐5‐D2‐2 11/9/2004 11:25 PDB GW µg/L 10 J^ 0.25 LJ 3.2 J^ 10 J 0.35 LJMNW‐05 (D2) D2 MNW5D2Q403 MNW5D2Q403 12/11/2003 11:43 unknown GW µg/L 4.3 = 0.9 J 6.8 = 0.2227 <
MNW‐05 (D3) 5/10/2020 0:00 unknownMNW‐05 (D3) D3 MNW‐5‐D3‐17‐022014 MNW‐5‐D3‐17 2/18/2014 11:30 PDB GW µg/L 9 = 0.5 U 4.8 = 16.1 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐0813 MNW‐5‐D3‐17 8/13/2013 9:40 PDB WG µg/L 8.2 = 0.9 = 3.8 = 19 = 0.5 UMNW‐05 (D3) D3 F6PG2 MNW‐5‐D3‐17 2/13/2013 0:00 PDB GW µg/L 8.7 = 0.74 = 3.3 = 16 = 0.5 UMNW‐05 (D3) D3 F6CE0 MNW‐5‐D3‐17 8/20/2012 11:35 PDB GW µg/L 10 = 0.74 = 3.0 = 22 = 0.5 UMNW‐05 (D3) D3 F5G37 MNW‐5‐D3‐17 2/28/2012 11:30 PDB GW µg/L 6.9 = 0.42 LJ 2.6 = 15 = 0.5 UMNW‐05 (D3) D3 F4EC8 MNW‐5‐D3‐17‐Q311 8/22/2011 11:25 PDB GW µg/L 13 = 5.0 U 4.9 LJ 27 = 2.0 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q111 MNW‐5‐D3‐17 2/14/2011 9:29 PDB GW µg/L 8.8 = 0.5 U 2.9 = 18.2 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q310 MNW‐5‐D3‐17‐Q310 9/8/2010 13:35 PDB GW µg/L 9.5 = 0.5 U 4.2 = 17.3 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 18 OF 64
011506
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐05 (D3) D3 MNW‐5‐D3‐17_100201 MNW‐5‐D3‐17 2/1/2010 12:49 PDB GW µg/L 10.6 = 0.5 U 6.2 = 15.8 = 0.5 UMNW‐05 (D3) D3 F3B22 MNW‐5‐D3‐17 10/26/2009 15:05 PDB GW µg/L 9.4 = 0.41 LJ 4.2 = 16 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q209 MNW‐5‐D3‐17 4/20/2009 9:48 PDB GW µg/L 9.1 J 0.5 J 3.7 J 17.8 J 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q408 MNW‐5‐D3‐17 10/7/2008 9:23 PDB GW µg/L 9.4 = 0.8 = 3.5 = 19.2 = 0.5 UMNW‐05 (D3) D3 F2RQ9 MNW‐5‐D3‐17 4/14/2008 0:00 PDB GW µg/L 14 = 1 = 4.7 = 18 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3‐17‐Q407 MNW‐5‐D3‐17 10/1/2007 10:55 PDB GW µg/L 10.8 = 0.9 = 3.9 = 19.6 = 0.5 UMNW‐05 (D3) D3 MNW‐5‐D3_070219 MNW‐5‐D3‐17 2/19/2007 10:00 PDB GW µg/L 10.4 JL 1 JL 3.4 JL 19.5 JL 0.5 UJMNW‐05 (D3) D3 F2683 MNW‐5‐D3‐17 8/28/2006 11:10 PDB GW µg/L 8.3 = 0.89 = 2.1 = 16 = 0.5 UMNW‐05 (D3) D3 F1YW2 MNW‐5‐D3‐17 2/6/2006 10:50 PDB GW µg/L 6 = 0.93 = 1.6 = 11 = 0.5 UMNW‐05 (D3) D3 F1YW1 MNW‐5‐D3‐12 2/6/2006 10:43 PDB GW µg/L 2.1 = 0.5 U 0.59 = 3.8 = 0.5 UMNW‐05 (D3) D3 F1P48 MNW‐5‐D3‐17 7/11/2005 13:49 PDB GW µg/L 6.9 = 0.86 = 1.6 = 11 = 0.5 UMNW‐05 (D3) D3 F1P47 MNW‐5‐D3‐12 7/11/2005 13:47 PDB GW µg/L 2.4 = 0.69 = 1.1 = 8.5 J 0.5 UMNW‐05 (D3) D3 F1P44 MNW‐5‐D3‐2 7/11/2005 13:40 PDB GW µg/L 1.7 = 0.25 LJ 0.46 LJ 3.1 = 0.5 UMNW‐05 (D3) D3 F1P45 MNW‐5‐D3‐7 7/11/2005 13:33 PDB GW µg/L 2.2 = 0.35 LJ 0.56 = 3.8 = 0.5 UMNW‐05 (D3) D3 F1DZ6 MNW‐5‐D3‐17 4/18/2005 14:08 PDB GW µg/L 6.7 = 1.3 = 1.7 = 13 = 0.5 UMNW‐05 (D3) D3 F1DZ5 MNW‐5‐D3‐12 4/18/2005 14:06 PDB GW µg/L 2.8 = 0.77 = 0.65 = 5.7 = 0.5 UMNW‐05 (D3) D3 F1DZ3 MNW‐5‐D3‐7 4/18/2005 14:02 PDB GW µg/L 2 = 0.48 LJ 0.49 LJ 4.0 = 0.5 UMNW‐05 (D3) D3 F1DZ2 MNW‐5‐D3‐2 4/18/2005 14:00 PDB GW µg/L 2.2 = 0.47 LJ 0.55 = 4.0 = 0.5 UMNW‐05 (D3) D3 F17R6 MNW‐5‐D3‐17 11/9/2004 11:25 PDB GW µg/L 4.9 = 0.68 = 1.1 = 10 = 0.5 UMNW‐05 (D3) D3 F17R5 MNW‐5‐D3‐12 11/9/2004 11:15 PDB GW µg/L 1.8 = 0.24 LJ 0.49 LJ 3.9 = 0.5 UMNW‐05 (D3) D3 F17R3 MNW‐5‐D3‐7 11/9/2004 11:10 PDB GW µg/L 2.1 = 0.24 LJ 0.53 = 4.3 = 0.5 UMNW‐05 (D3) D3 F17R2 MNW‐5‐D3‐2 11/9/2004 11:05 PDB GW µg/L 2 = 0.22 LJ 0.42 LJ 4.0 = 0.5 UMNW‐05 (D3) D3 MNW5D3Q403 MNW5D3Q403 12/10/2003 16:03 unknown GW µg/L 3.7 = 0.7936 < 7.1 = 0.2227 <
MNW‐05 (D4) 5/10/2020 0:00 unknownMNW‐05 (D4) D4 MNW‐5‐D4‐7‐022014 MNW‐5‐D4‐7 2/18/2014 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F6PG4 MNW‐5‐D4‐7‐FD 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F6PG3 MNW‐5‐D4‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJvMNW‐05 (D4) D4 F5G39 MNW‐5‐D4‐7‐FD 2/28/2012 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F5G38 MNW‐5‐D4‐7 2/28/2012 9:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐5‐Q111 MNW‐5‐D4‐5 2/14/2011 9:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7_100201 MNW‐5‐D4‐7 2/1/2010 12:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7‐Q209 MNW‐5‐D4‐7 4/20/2009 9:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7‐Q408 MNW‐5‐D4‐7 10/7/2008 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F2RR0 MNW‐5‐D4‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4‐7‐Q407 MNW‐5‐D4‐7 10/1/2007 11:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 MNW‐5‐D4_070219 MNW‐5‐D4‐7 2/19/2007 10:17 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐05 (D4) D4 F2684 MNW‐5‐D4‐7 8/28/2006 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1YW3 MNW‐5‐D4‐7 2/6/2006 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P52 MNW‐5‐D4‐17 7/11/2005 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P51 MNW‐5‐D4‐12 7/11/2005 14:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P50 MNW‐5‐D4‐7 7/11/2005 14:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1P49 MNW‐5‐D4‐2 7/11/2005 14:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1E00 MNW‐5‐D4‐17 4/18/2005 14:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1DZ9 MNW‐5‐D4‐12 4/18/2005 14:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1DZ8 MNW‐5‐D4‐7 4/18/2005 14:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐05 (D4) D4 F1DZ7 MNW‐5‐D4‐2 4/18/2005 14:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 19 OF 64
011507
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐06 (D1) 5/10/2020 0:00 unknown
MNW‐06 (D1) D1 F6PG6 MNW‐6‐D1‐7‐FD 2/13/2013 0:00 PDB GW µg/L 0.52 = 0.5 U 0.5 U 2.1 = 0.5 UMNW‐06 (D1) D1 F6PG5 MNW‐6‐D1‐7 2/13/2013 0:00 PDB GW µg/L 0.62 = 0.5 U 0.16 LJ 2.4 = 0.5 UJvMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q111‐FD MNW‐6‐D1‐7 2/14/2011 9:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1 = 0.5 UMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q111 MNW‐6‐D1‐7 2/14/2011 8:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1 = 0.5 UMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q209 MNW‐6‐D1‐7 4/20/2009 7:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 MNW‐6‐D1‐7‐Q407 MNW‐6‐D1‐7 10/2/2007 11:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F1P56 MNW‐6‐D1‐17 7/12/2005 8:15 PDB GW µg/L 0.5 U 0.076 LJ 0.5 U 0.13 LJ 0.5 UMNW‐06 (D1) D1 F1P55 MNW‐6‐D1‐12 7/12/2005 8:14 PDB GW µg/L 0.086 LJ 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐06 (D1) D1 F1P54 MNW‐6‐D1‐7 7/12/2005 8:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.11 LJ 0.5 UMNW‐06 (D1) D1 F1P53 MNW‐6‐D1‐2 7/12/2005 8:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.1 LJ 0.5 UMNW‐06 (D1) D1 F1E04 MNW‐6‐D1‐17 4/19/2005 14:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UMNW‐06 (D1) D1 F1E03 MNW‐6‐D1‐12 4/19/2005 14:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.18 LJ 0.5 UMNW‐06 (D1) D1 F1E02 MNW‐6‐D1‐7 4/19/2005 14:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.22 LJ 0.5 UMNW‐06 (D1) D1 F1E01 MNW‐6‐D1‐2 4/19/2005 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.19 LJ 0.5 UMNW‐06 (D1) D1 F17S0 MNW‐6‐D1‐17 11/10/2004 8:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F17R9 MNW‐6‐D1‐12 11/10/2004 8:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F17R8 MNW‐6‐D1‐7 11/10/2004 8:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D1) D1 F17R7 MNW‐6‐D1‐2 11/10/2004 8:10 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐06 (D1) D1 MNW6D1Q403 MNW6D1Q403 11/14/2003 15:44 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐06 (D2) 5/10/2020 0:00 unknownMNW‐06 (D2) D2 F6PG7 MNW‐6‐D2‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJvMNW‐06 (D2) D2 MNW‐6‐D2‐7‐Q111 MNW‐6‐D2‐7 2/14/2011 8:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 MNW‐6‐D2‐7‐Q209 MNW‐6‐D2‐7 4/20/2009 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 MNW‐6‐D2‐7‐Q407 MNW‐6‐D2‐7 10/2/2007 11:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F1P60 MNW‐6‐D2‐17 7/12/2005 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.091 LJ 0.5 UMNW‐06 (D2) D2 F1P59 MNW‐6‐D2‐12 7/12/2005 8:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 UMNW‐06 (D2) D2 F1P58 MNW‐6‐D2‐7 7/12/2005 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐06 (D2) D2 F1P57 MNW‐6‐D2‐2 7/12/2005 8:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐06 (D2) D2 F1E08 MNW‐6‐D2‐17 4/19/2005 14:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F1E07 MNW‐6‐D2‐12 4/19/2005 14:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F1E06 MNW‐6‐D2‐7 4/19/2005 14:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐06 (D2) D2 F1E05 MNW‐6‐D2‐2 4/19/2005 14:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐06 (D2) D2 F17D6 MNW‐6‐D2 11/9/2004 11:40 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.2 LJ 0.5 UMNW‐06 (D2) D2 F17S4 MNW‐6‐D2‐17 11/9/2004 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F17S3 MNW‐6‐D2‐12 11/9/2004 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 F17S2 MNW‐6‐D2‐7 11/9/2004 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D2) D2 MNW6D2Q403 MNW6D2Q403 11/17/2003 10:08 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.3 J
MNW‐06 (D3) 5/10/2020 0:00 unknownMNW‐06 (D3) D3 MNW‐6‐D3‐7‐022014 MNW‐6‐D3‐7 2/17/2014 12:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F6PG8 MNW‐6‐D3‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F5G40 MNW‐6‐D3‐7 2/28/2012 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7‐Q111 MNW‐6‐D3‐7 2/14/2011 8:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7_100201 MNW‐6‐D3‐7 2/1/2010 13:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7‐Q209 MNW‐6‐D3‐7 4/20/2009 8:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW‐6‐D3‐7‐Q407 MNW‐6‐D3‐7 10/2/2007 11:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 20 OF 64
011508
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐06 (D3) D3 F1P64 MNW‐6‐D3‐17 7/12/2005 9:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1P63 MNW‐6‐D3‐12 7/12/2005 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1P62 MNW‐6‐D3‐7 7/12/2005 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1P61 MNW‐6‐D3‐2 7/12/2005 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.084 LJMNW‐06 (D3) D3 F1E12 MNW‐6‐D3‐17 4/19/2005 15:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1E11 MNW‐6‐D3‐12 4/19/2005 15:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1E10 MNW‐6‐D3‐7 4/19/2005 15:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F1E09 MNW‐6‐D3‐2 4/19/2005 15:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S8 MNW‐6‐D3‐17 11/10/2004 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S7 MNW‐6‐D3‐12 11/10/2004 8:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S6 MNW‐6‐D3‐7 11/10/2004 7:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 F17S5 MNW‐6‐D3‐2 11/10/2004 7:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐06 (D3) D3 MNW6D3Q403 MNW6D3Q403 11/17/2003 15:16 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.3 J
MNW‐07 (D4) 5/10/2020 0:00 unknownMNW‐07 (D4) D4 F6PG9 MNW‐7‐D4‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F3S26 MNW‐7‐D4‐7 2/15/2011 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4‐7‐Q209 MNW‐7‐D4‐7 4/20/2009 12:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4‐7‐Q408 MNW‐7‐D4‐7 10/7/2008 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F2RR1 MNW‐7‐D4‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4‐7‐Q407 MNW‐7‐D4‐7 10/2/2007 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW‐7‐D4_070219 MNW‐7‐D4‐7 2/19/2007 10:54 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐07 (D4) D4 F2685 MNW‐7‐D4‐7 8/28/2006 14:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P96 MNW‐7‐D4‐17 7/12/2005 12:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P95 MNW‐7‐D4‐12 7/12/2005 12:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P94 MNW‐7‐D4‐7 7/12/2005 12:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1P92 MNW‐7‐D4‐2 7/12/2005 12:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E44 MNW‐7‐D4‐17 4/18/2005 15:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E43 MNW‐7‐D4‐12 4/18/2005 15:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E40 MNW‐7‐D4‐2 4/18/2005 15:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F1E42 MNW‐7‐D4‐7 4/18/2005 14:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17T3 MNW‐7‐D4‐17 11/10/2004 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17T2 MNW‐7‐D4‐12 11/10/2004 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17T1 MNW‐7‐D4‐7 11/10/2004 8:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 F17S9 MNW‐7‐D4‐2 11/10/2004 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐07 (D4) D4 MNW7Q403 MNW7Q403 11/22/2003 17:00 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐08 (I1) 5/10/2020 0:00 unknownMNW‐08 (I1) I1 F6PH0 MNW‐8‐I1‐5 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F6PH1 MNW‐8‐I1‐5‐FD 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 MNW‐8‐I1‐5‐Q111 MNW‐8‐I1‐5 2/16/2011 13:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1NG3 MNW‐8‐I1‐12 7/12/2005 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1NG2 MNW‐8‐I1‐7 7/12/2005 8:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1NG1 MNW‐8‐I1‐2 7/12/2005 8:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1DC4 MNW‐8‐I1‐12 4/20/2005 9:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1DC3 MNW‐8‐I1‐7 4/20/2005 9:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F1DC2 MNW‐8‐I1‐2 4/20/2005 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F17J3 MNW‐8‐I1‐12 11/9/2004 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 21 OF 64
011509
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐08 (I1) I1 F17J2 MNW‐8‐I1‐7 11/9/2004 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 F17J1 MNW‐8‐I1‐2 11/9/2004 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I1) I1 MNW8I1Q403 MNW8I1Q403 12/14/2003 14:45 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐08 (I2) 5/10/2020 0:00 unknownMNW‐08 (I2) I2 MNW‐8‐I2‐7‐022014 MNW‐8‐I2‐7 2/17/2014 8:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐0813 MNW‐8‐I2‐7 8/13/2013 8:45 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F6PH2 MNW‐8‐I2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F6CA4 MNW‐8‐I2‐7 8/20/2012 9:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F5G41 MNW‐8‐I2‐7 2/28/2012 8:00 PDB GW µg/L 4.7 = 0.61 = 2 = 11 = 0.5 UMNW‐08 (I2) I2 F4EC9 MNW‐8‐I2‐7‐Q311 8/23/2011 7:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q111 MNW‐8‐I2‐7 2/16/2011 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q310 MNW‐8‐I2‐7‐Q310 9/8/2010 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7_100201 MNW‐8‐I2‐7 2/1/2010 10:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F3B36 MNW‐8‐I2‐7 10/26/2009 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q209 MNW‐8‐I2‐7 4/21/2009 7:36 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐08 (I2) I2 MNW‐8‐I2‐7‐Q407 MNW‐8‐I2‐7 10/2/2007 8:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG7 MNW‐8‐I2‐17 7/12/2005 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG6 MNW‐8‐I2‐12 7/12/2005 8:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG5 MNW‐8‐I2‐7 7/12/2005 8:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1NG4 MNW‐8‐I2‐2 7/12/2005 8:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC8 MNW‐8‐I2‐17 4/20/2005 9:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC7 MNW‐8‐I2‐12 4/20/2005 9:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC6 MNW‐8‐I2‐7 4/20/2005 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F1DC5 MNW‐8‐I2‐2 4/20/2005 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17D7 MNW‐8‐I2 11/16/2004 8:50 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.44 LJ 0.5 UMNW‐08 (I2) I2 F17J7 MNW‐8‐I2‐17 11/9/2004 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17J6 MNW‐8‐I2‐12 11/9/2004 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17J5 MNW‐8‐I2‐7 11/9/2004 10:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 F17J4 MNW‐8‐I2‐2 11/9/2004 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐08 (I2) I2 MNW8I2Q403 MNW8I2Q403 12/14/2003 11:26 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐09 (D1) 5/10/2020 0:00 unknownMNW‐09 (D1) D1 MNW‐9‐D1‐2‐022014 MNW‐9‐D1‐2 2/17/2014 10:15 PDB GW µg/L 1 = 0.5 U 0.6 = 3.1 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐0813 MNW‐9‐D1‐2 8/13/2013 9:58 PDB WG µg/L 1.3 = 0.5 U 1.9 = 3.1 = 0.5 UMNW‐09 (D1) D1 F6PH3 MNW‐9‐D1‐2 2/18/2013 0:00 PDB GW µg/L 0.83 = 0.5 U 0.56 = 2.9 = 0.5 UMNW‐09 (D1) D1 F6CE1 MNW‐9‐D1‐2 8/20/2012 13:49 PDB GW µg/L 0.92 = 0.048 LJ 0.53 = 4.6 J^ 0.5 UMNW‐09 (D1) D1 F5G42 MNW‐9‐D1‐2 2/27/2012 12:57 PDB GW µg/L 0.57 = 0.5 U 0.29 LJ 2.3 = 0.5 UMNW‐09 (D1) D1 F4ED1 MNW‐9‐D1‐2‐Q311 8/22/2011 9:25 PDB GW µg/L 1.7 LJ 5.0 U 1.6 LJ 5.7 = 2.0 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q111 MNW‐9‐D1‐2 2/16/2011 11:28 PDB GW µg/L 0.7 = 0.5 U 0.5 U 3.4 = 0.5 UMNW‐09 (D1) D1 F3LQ7 MNW‐9‐D1‐2‐Q310‐FD 9/2/2010 14:10 PDB GW µg/L 0.96 = 0.5 U 0.39 LJ 4.4 = 0.5 UMNW‐09 (D1) D1 F3LQ6 MNW‐9‐D1‐2‐Q310 9/2/2010 13:10 PDB GW µg/L 1 = 0.5 U 0.42 LJ 4.8 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2_100202‐FD MNW‐9‐D1‐2 2/2/2010 11:30 PDB GW µg/L 0.8 = 0.5 U 0.6 = 3.3 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2_100202 MNW‐9‐D1‐2 2/2/2010 10:30 PDB GW µg/L 0.8 = 0.5 U 0.6 = 3.4 = 0.5 UMNW‐09 (D1) D1 F3B24 MNW‐9‐D1‐2 10/26/2009 8:45 PDB GW µg/L 1.2 = 0.5 U 0.62 = 5.2 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐FD‐Q209 MNW‐9‐D1‐2‐FD 4/20/2009 14:00 PDB GW µg/L 1.3 J 0.5 U 0.6 J 5.0 J 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q209 MNW‐9‐D1‐2 4/20/2009 13:53 PDB GW µg/L 1.2 J 0.5 U 0.7 J 5.2 J 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q408 MNW‐9‐D1‐2 10/6/2008 10:15 PDB GW µg/L 5.1 = 0.5 U 7.2 = 2.2 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 22 OF 64
011510
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐09 (D1) D1 F2RR4 MNW‐9‐D1‐2 4/14/2008 0:00 PDB GW µg/L 2.3 = 0.5 U 2.1 = 5.6 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐2‐Q407 MNW‐9‐D1‐2 10/1/2007 11:31 PDB GW µg/L 3.8 = 0.5 U 4 = 8.8 = 0.5 UMNW‐09 (D1) D1 MNW‐9‐D1‐070222 MNW‐9‐D1‐2 2/22/2007 11:00 PDB GW µg/L 0.8 = 0.5 U 0.5 U 4.6 = 0.5 UMNW‐09 (D1) D1 F2686 MNW‐9‐D1‐2 8/29/2006 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 3.4 = 0.5 UMNW‐09 (D1) D1 F1YM3 MNW‐9‐D1‐17 2/6/2006 10:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.9 = 0.5 UMNW‐09 (D1) D1 F1YM2 MNW‐9‐D1‐12 2/6/2006 10:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2 = 0.5 UMNW‐09 (D1) D1 F1YM0 MNW‐9‐D1‐7 2/6/2006 10:38 PDB GW µg/L 0.51 = 0.5 U 0.5 U 3.2 = 0.5 UMNW‐09 (D1) D1 F1YL9 MNW‐9‐D1‐2 2/6/2006 10:37 PDB GW µg/L 0.69 = 0.5 U 0.5 U 4.2 = 0.5 UMNW‐09 (D1) D1 F1NJ0 MNW‐9‐D1‐17 7/11/2005 14:11 PDB GW µg/L 1.1 = 0.5 U 0.5 U 5.3 = 0.11 LJMNW‐09 (D1) D1 F1NH9 MNW‐9‐D1‐12 7/11/2005 14:09 PDB GW µg/L 1.7 = 0.5 U 0.5 U 8 = 0.5 UMNW‐09 (D1) D1 F1NH8 MNW‐9‐D1‐7 7/11/2005 14:07 PDB GW µg/L 1.2 = 0.5 U 0.5 U 6.2 = 0.5 UMNW‐09 (D1) D1 F1NH7 MNW‐9‐D1‐2 7/11/2005 14:05 PDB GW µg/L 3.4 = 0.5 U 0.13 LJ 15 = 0.5 UMNW‐09 (D1) D1 F1DA3 MNW‐9‐D1 4/20/2005 12:05 LFS GW µg/L 0.35 LJ 0.5 U 0.5 U 2.9 = 0.5 UMNW‐09 (D1) D1 F1DE1 MNW‐9‐D1‐17 4/19/2005 14:34 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 1.3 = 0.5 UMNW‐09 (D1) D1 F1DE0 MNW‐9‐D1‐12 4/19/2005 14:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 UMNW‐09 (D1) D1 F1DD9 MNW‐9‐D1‐7 4/19/2005 14:28 PDB GW µg/L 0.34 LJ 0.5 U 0.5 U 1.5 = 0.5 UMNW‐09 (D1) D1 F1DD8 MNW‐9‐D1‐2 4/19/2005 14:24 PDB GW µg/L 0.4 LJ 0.5 U 0.5 U 2.2 = 0.5 U
MNW‐09 (D2) 5/10/2020 0:00 unknownMNW‐09 (D2) D2 F6PH4 MNW‐9‐D2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q111 MNW‐9‐D2‐7 2/16/2011 11:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q209 MNW‐9‐D2‐7 4/20/2009 13:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q408 MNW‐9‐D2‐7 10/6/2008 10:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F2RR6 MNW‐9‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐7‐Q407 MNW‐9‐D2‐7 10/1/2007 11:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 MNW‐9‐D2‐070222 MNW‐9‐D2‐7 2/22/2007 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F2688 MNW‐9‐D2‐7 8/29/2006 11:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1YM4 MNW‐9‐D2‐2 2/6/2006 10:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ4 MNW‐9‐D2‐17 7/11/2005 14:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ3 MNW‐9‐D2‐12 7/11/2005 14:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ2 MNW‐9‐D2‐7 7/11/2005 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1NJ1 MNW‐9‐D2‐2 7/11/2005 14:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1DE5 MNW‐9‐D2‐17 4/19/2005 14:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1DE4 MNW‐9‐D2‐12 4/19/2005 14:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1DE3 MNW‐9‐D2‐7 4/19/2005 14:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (D2) D2 F1DE2 MNW‐9‐D2‐2 4/19/2005 14:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐09 (I1) 5/10/2020 0:00 unknownMNW‐09 (I1) I1 F6PH5 MNW‐9‐I1‐5 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐5‐Q111 MNW‐9‐I1‐5 2/16/2011 11:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐7‐Q209 MNW‐9‐I1‐7 4/20/2009 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐7‐Q408 MNW‐9‐I1‐7 10/6/2008 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F2RR2 MNW‐9‐I1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1‐7‐Q407 MNW‐9‐I1‐7 10/1/2007 12:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW‐9‐I1_070219 MNW‐9‐I1‐7 2/19/2007 12:53 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐09 (I1) I1 F2689 MNW‐9‐I1‐7 8/29/2006 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1YL7 MNW‐9‐I1‐7 2/6/2006 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1NH0 MNW‐9‐I1‐12 7/11/2005 13:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 23 OF 64
011511
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐09 (I1) I1 F1NG9 MNW‐9‐I1‐7 7/11/2005 13:26 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐09 (I1) I1 F1NG8 MNW‐9‐I1‐2 7/11/2005 13:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.12 LJMNW‐09 (I1) I1 F1DD1 MNW‐9‐I1‐12 4/19/2005 13:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1DD0 MNW‐9‐I1‐7 4/19/2005 13:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F1DC9 MNW‐9‐I1‐2 4/19/2005 13:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F17K0 MNW‐9‐I1‐12 11/8/2004 12:41 PDB GW µg/L 0.5 UJv 0.5 UJv 0.5 UJv 0.5 UJv 0.5 UJvMNW‐09 (I1) I1 F17J9 MNW‐9‐I1‐7 11/8/2004 12:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 F17J8 MNW‐9‐I1‐2 11/8/2004 12:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐09 (I1) I1 MNW9I1Q403 MNW9I1Q403 12/17/2003 14:55 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐09 (I2) 5/10/2020 0:00 unknownMNW‐09 (I2) I2 MNW‐9‐I2‐17‐022014 MNW‐9‐I2‐17 2/17/2014 10:07 PDB GW µg/L 1.3 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐0813 MNW‐9‐I2‐17 8/13/2013 10:07 PDB WG µg/L 1.3 = 0.5 U 0.6 = 3.8 = 0.5 UMNW‐09 (I2) I2 F6PH6 MNW‐9‐I2‐17 2/18/2013 0:00 PDB GW µg/L 1.6 = 0.5 U 0.37 LJ 3.6 = 0.5 UMNW‐09 (I2) I2 F6CE2 MNW‐9‐I2‐17 8/20/2012 13:46 PDB GW µg/L 1.6 = 0.032 LJ 0.25 LJ 5.4 J^ 0.5 UMNW‐09 (I2) I2 F5G43 MNW‐9‐I2‐17 2/27/2012 12:47 PDB GW µg/L 1.5 = 0.5 U 0.5 U 4.5 = 0.5 UMNW‐09 (I2) I2 F4ED0 MNW‐9‐12‐17‐FD‐Q311 8/22/2011 9:18 PDB GW µg/L 2.7 LJ 5.0 U 5.0 U 9.2 = 2.0 UMNW‐09 (I2) I2 F4ED2 MNW‐9‐I2‐17‐Q311 8/22/2011 9:17 PDB GW µg/L 2.6 LJ 5.0 U 5.0 U 8.9 = 2.0 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q111 MNW‐9‐I2‐17 2/16/2011 11:38 PDB GW µg/L 1.9 = 0.5 U 0.5 U 7.2 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q310 MNW‐9‐I2‐17‐Q310 9/7/2010 8:37 PDB GW µg/L 2.9 = 0.5 U 0.5 U 9.4 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17_100202 MNW‐9‐I2‐17 2/2/2010 10:40 PDB GW µg/L 2.9 = 0.5 U 0.5 U 12.1 = 0.5 UMNW‐09 (I2) I2 F3B23 MNW‐9‐I2‐17 10/26/2009 8:38 PDB GW µg/L 2.7 = 0.5 U 0.5 U 11 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q209 MNW‐9‐I2‐17 4/20/2009 14:16 PDB GW µg/L 3.2 J 0.5 U 0.5 U 13.8 J 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q408 MNW‐9‐I2‐17 10/6/2008 10:39 PDB GW µg/L 4.4 = 0.5 U 0.5 U 16.2 = 0.5 UMNW‐09 (I2) I2 F2RR3 MNW‐9‐I2‐17 4/14/2008 0:00 PDB GW µg/L 4.9 = 0.5 U 0.14 LJ 19 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2‐17‐Q407 MNW‐9‐I2‐17 10/1/2007 11:53 PDB GW µg/L 4.1 = 0.5 U 0.5 U 16.4 = 0.5 UMNW‐09 (I2) I2 MNW‐9‐I2_070219 MNW‐9‐I2‐17 2/19/2007 13:00 PDB GW µg/L 3.6 JL 0.5 UJ 0.5 UJ 18.8 JL 0.5 UJMNW‐09 (I2) I2 F2690 MNW‐9‐I2‐17 8/29/2006 11:00 PDB GW µg/L 2.5 = 0.5 U 0.5 U 17 = 0.5 UMNW‐09 (I2) I2 F1YL8 MNW‐9‐I2‐17 2/6/2006 10:26 PDB GW µg/L 3.6 = 0.5 U 0.5 U 20 = 0.5 UMNW‐09 (I2) I2 F1NH6 MNW‐9‐I2‐17 7/11/2005 13:49 PDB GW µg/L 4.9 = 0.5 U 0.18 LJ 21 = 0.14 LJMNW‐09 (I2) I2 F1NH5 MNW‐9‐I2‐12 7/11/2005 13:42 PDB GW µg/L 4.7 = 0.5 U 0.17 LJ 21 J 0.5 UMNW‐09 (I2) I2 F1NH3 MNW‐9‐I2‐7 7/11/2005 13:39 PDB GW µg/L 3.4 = 0.5 U 0.12 LJ 16 = 0.13 LJMNW‐09 (I2) I2 F1NH2 MNW‐9‐I2‐2 7/11/2005 13:37 PDB GW µg/L 3.3 = 0.5 U 0.12 LJ 18 = 0.16 LJMNW‐09 (I2) I2 F1DA1 MNW‐9‐I2 4/20/2005 9:20 LFS GW µg/L 2.6 = 0.5 U 0.5 U 14 J 0.5 UMNW‐09 (I2) I2 F1DD7 MNW‐9‐I2‐17 4/19/2005 13:54 PDB GW µg/L 4.3 = 0.5 U 0.5 U 22 = 0.5 UMNW‐09 (I2) I2 F1DD6 MNW‐9‐I2‐12 4/19/2005 13:50 PDB GW µg/L 3.6 = 0.5 U 0.11 LJ 18 J 0.5 UMNW‐09 (I2) I2 F1DD4 MNW‐9‐I2‐7 4/19/2005 13:44 PDB GW µg/L 3.5 = 0.5 U 0.11 LJ 18 = 0.5 UMNW‐09 (I2) I2 F1DD3 MNW‐9‐I2‐2 4/19/2005 13:40 PDB GW µg/L 3.3 = 0.5 U 0.11 LJ 16 = 0.5 UMNW‐09 (I2) I2 F17K6 MNW‐9‐I2‐17 11/8/2004 13:35 PDB GW µg/L 3.9 = 0.5 U 0.5 U 19 = 0.5 UMNW‐09 (I2) I2 F17K5 MNW‐9‐I2‐12 11/8/2004 13:25 PDB GW µg/L 3.9 = 0.5 U 0.5 U 19 = 0.5 UMNW‐09 (I2) I2 F17K3 MNW‐9‐I2‐7 11/8/2004 13:15 PDB GW µg/L 3.8 = 0.5 U 0.5 U 17 = 0.5 UMNW‐09 (I2) I2 F17K2 MNW‐9‐I2‐2 11/8/2004 13:00 PDB GW µg/L 3.3 = 0.5 U 0.5 U 7.9 = 0.37 LJMNW‐09 (I2) I2 MNW9I2Q403 MNW9I2Q403 12/18/2003 17:05 unknown GW µg/L 2.2 = 0.7936 < 11 = 0.2227 <
MNW‐10 (I1) 5/10/2020 0:00 unknownMNW‐10 (I1) I1 MNW‐10‐I1‐2‐Q209 MNW‐10‐I1‐2 4/20/2009 10:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 MNW‐10‐I1‐2‐Q408 MNW‐10‐I1‐2 10/6/2008 10:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F2RR7 MNW‐10‐I1‐2 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 24 OF 64
011512
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐10 (I1) I1 MNW‐10‐I1‐2‐Q407 MNW‐10‐I1‐2 10/1/2007 11:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 MNW‐10‐I1_070219 MNW‐10‐I1‐2 2/19/2007 13:36 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐10 (I1) I1 F2644 MNW‐10‐I1‐2 8/28/2006 12:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1YM5 MNW‐10‐I1‐2 2/6/2006 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1NJ7 MNW‐10‐I1‐12 7/12/2005 8:48 PDB GW µg/L 0.34 LJv 0.5 U 0.084 LJv 0.067 LJ 0.5 UMNW‐10 (I1) I1 F1NJ6 MNW‐10‐I1‐7 7/12/2005 8:47 PDB GW µg/L 0.31 LJ 0.5 U 0.5 U 0.076 LJ 0.5 UMNW‐10 (I1) I1 F1NJ5 MNW‐10‐I1‐2 7/12/2005 8:46 PDB GW µg/L 0.44 LJ 0.5 U 0.12 LJ 0.082 LJ 0.056 LJMNW‐10 (I1) I1 F1DE8 MNW‐10‐I1‐12 4/20/2005 10:36 PDB GW µg/L 0.33 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1DE7 MNW‐10‐I1‐7 4/20/2005 10:33 PDB GW µg/L 0.35 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F1DE6 MNW‐10‐I1‐2 4/20/2005 10:30 PDB GW µg/L 0.35 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F17H2 MNW‐10‐I1‐12 11/8/2004 10:10 PDB GW µg/L 0.25 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F17H1 MNW‐10‐I1‐7 11/8/2004 10:03 PDB GW µg/L 0.31 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 F17H0 MNW‐10‐I1‐2 11/8/2004 9:57 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I1) I1 MNW10I1Q403 MNW10I1Q403 12/20/2003 10:43 unknown GW µg/L 0.4 J 0.7936 < 0.3733 < 0.2227 <
MNW‐10 (I2) 5/10/2020 0:00 unknownMNW‐10 (I2) I2 F6PB3 MNW‐10‐I2‐7 2/18/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F3S44 MNW‐10‐I2‐7 2/15/2011 10:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2‐7‐Q209 MNW‐10‐I2‐7 4/20/2009 11:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2‐7‐Q408 MNW‐10‐I2‐7 10/6/2008 11:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F2RR8 MNW‐10‐I2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2‐7‐Q407 MNW‐10‐I2‐7 10/1/2007 11:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW‐10‐I2_070219 MNW‐10‐I2‐7 2/19/2007 13:45 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐10 (I2) I2 F2645 MNW‐10‐I2‐7 8/28/2006 12:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1YM6 MNW‐10‐I2‐7 2/6/2006 9:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NK1 MNW‐10‐I2‐17 7/12/2005 8:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NK0 MNW‐10‐I2‐12 7/12/2005 8:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NJ9 MNW‐10‐I2‐7 7/12/2005 8:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1NJ8 MNW‐10‐I2‐2 7/12/2005 8:55 PDB GW µg/L 0.17 LJ 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DF2 MNW‐10‐I2‐17 4/20/2005 10:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DF1 MNW‐10‐I2‐12 4/20/2005 10:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DF0 MNW‐10‐I2‐7 4/20/2005 10:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F1DE9 MNW‐10‐I2‐2 4/20/2005 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17D2 MNW‐10‐I2 11/16/2004 15:10 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H6 MNW‐10‐I2‐17 11/8/2004 10:49 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H5 MNW‐10‐I2‐12 11/8/2004 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H4 MNW‐10‐I2‐7 11/8/2004 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 F17H3 MNW‐10‐I2‐2 11/8/2004 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐10 (I2) I2 MNW10I2Q403 MNW10I2Q403 12/20/2003 12:05 unknown GW µg/L 0.2937 < 0.7936 < 0.3733 < 0.2227 <
MNW‐11 (D1) 5/10/2020 0:00 unknownMNW‐11 (D1) D1 MNW‐11‐D1‐2‐022014 MNW‐11‐D1‐2 2/17/2014 12:20 PDB GW µg/L 10.2 = 0.5 U 11.8 = 23.4 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐0813 MNW‐11‐D1‐2 8/13/2013 9:40 PDB WG µg/L 8.9 = 0.5 U 6.2 = 34.8 = 0.5 UMNW‐11 (D1) D1 F6PB4 MNW‐11‐D1‐2 2/19/2013 0:00 PDB GW µg/L 11 = 0.5 U 9.3 = 36 = 0.14 LJMNW‐11 (D1) D1 F6CE3 MNW‐11‐D1‐2 8/20/2012 13:30 PDB GW µg/L 11 = 0.5 U 5.6 = 46 = 0.5 UMNW‐11 (D1) D1 F5G10DL MNW‐11‐D1‐2 2/27/2012 10:10 PDB GW µg/L 27 =MNW‐11 (D1) D1 F5G10 MNW‐11‐D1‐2 2/27/2012 10:10 PDB GW µg/L 6.3 = 0.5 U 4.2 = 0.5 UMNW‐11 (D1) D1 F4EA8 MNW‐11‐D1‐2‐Q311 8/22/2011 13:17 PDB GW µg/L 10 = 5.0 U 6.6 = 46 = 2.0 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 25 OF 64
011513
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q111 MNW‐11‐D1‐2 2/16/2011 10:30 PDB GW µg/L 8 = 0.5 U 5.6 J 35.2 = 0.5 UMNW‐11 (D1) D1 F3LQ8 MNW‐11‐D1‐2‐Q310 9/2/2010 13:15 PDB GW µg/L 5.9 = 0.5 U 3.8 = 31 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2_100202 MNW‐11‐D1‐2 2/2/2010 9:50 PDB GW µg/L 7.2 = 0.5 U 4.1 = 33.6 = 0.5 UMNW‐11 (D1) D1 F3B26 MNW‐11‐D1‐2 10/26/2009 11:03 PDB GW µg/L 6.9 = 0.5 U 3.7 = 25 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q209 MNW‐11‐D1‐2 4/20/2009 13:30 PDB GW µg/L 6.8 = 0.5 U 3.8 = 33.1 J 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q408 MNW‐11‐D1‐2 10/6/2008 9:35 PDB GW µg/L 7.1 = 0.5 U 3.1 = 32.1 J 0.5 UMNW‐11 (D1) D1 F2RS2 MNW‐11‐D1‐2 4/14/2008 0:00 PDB GW µg/L 7.5 = 0.5 U 4.8 = 20 = 0.5 UMNW‐11 (D1) D1 F2RS3 MNW‐11‐D1‐7 4/14/2008 0:00 PDB GW µg/L 8.6 = 0.5 U 6.2 = 24 = 0.5 UMNW‐11 (D1) D1 F2RS5 MNW‐11‐D1‐17 4/14/2008 0:00 PDB GW µg/L 8.5 = 0.5 U 6 = 25 = 0.5 UMNW‐11 (D1) D1 F2RS4 MNW‐11‐D1‐12 4/14/2008 0:00 PDB GW µg/L 7.1 = 0.5 U 4.8 = 35 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐17‐Q407 MNW‐11‐D1‐17 10/1/2007 9:30 PDB GW µg/L 6.6 = 0.5 U 4.8 = 26.6 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐12‐Q407 MNW‐11‐D1‐12 10/1/2007 9:27 PDB GW µg/L 6.7 = 0.5 U 4.5 = 25.6 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐7‐Q407 MNW‐11‐D1‐7 10/1/2007 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.8 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐2‐Q407 MNW‐11‐D1‐2 10/1/2007 9:20 PDB GW µg/L 6.3 = 0.5 U 4.2 = 28.1 = 0.5 UMNW‐11 (D1) D1 MNW‐11‐D1‐17_070219 MNW‐11‐D1‐17 2/19/2007 14:40 PDB GW µg/L 5.5 JL 0.5 UJ 4.4 JL 22.7 JL 0.5 UJMNW‐11 (D1) D1 MNW‐11‐D1‐12_070219 MNW‐11‐D1‐12 2/19/2007 14:38 PDB GW µg/L 5.5 JL 0.5 UJ 4.3 JL 22.6 JL 0.5 UJMNW‐11 (D1) D1 MNW‐11‐D1‐7_070219 MNW‐11‐D1‐7 2/19/2007 14:35 PDB GW µg/L 5.4 JL 0.5 UJ 4.2 JL 22.9 JL 0.5 UJMNW‐11 (D1) D1 MNW‐11‐D1‐2_070219 MNW‐11‐D1‐2 2/19/2007 14:25 PDB GW µg/L 5.6 JL 0.5 UJ 4.2 JL 24.9 JL 0.5 UJMNW‐11 (D1) D1 F2646DL MNW‐11‐D1‐2 8/29/2006 10:20 PDB GW µg/L 32 =MNW‐11 (D1) D1 F2646 MNW‐11‐D1‐2 8/29/2006 10:20 PDB GW µg/L 4.6 = 0.5 U 0.68 = 0.5 UMNW‐11 (D1) D1 F1YN4 MNW‐11‐D1‐17 2/6/2006 10:00 PDB GW µg/L 5.1 = 0.5 U 5.6 = 16 = 0.5 UMNW‐11 (D1) D1 F1YN3 MNW‐11‐D1‐12 2/6/2006 9:56 PDB GW µg/L 5.2 = 0.5 U 5 = 16 = 0.5 UMNW‐11 (D1) D1 F1YN2 MNW‐11‐D1‐7 2/6/2006 9:53 PDB GW µg/L 4.9 = 0.5 U 4.4 = 17 J 0.5 UMNW‐11 (D1) D1 F1YN1 MNW‐11‐D1‐2 2/6/2006 9:50 PDB GW µg/L 5 = 0.5 U 4.1 = 20 = 0.5 UMNW‐11 (D1) D1 F1NL2 MNW‐11‐D1‐17 7/11/2005 8:33 PDB GW µg/L 3 = 0.5 U 0.14 LJ 13 = 0.5 UMNW‐11 (D1) D1 F1NL1 MNW‐11‐D1‐12 7/11/2005 8:30 PDB GW µg/L 2.2 = 0.5 U 0.5 U 11 = 0.5 UMNW‐11 (D1) D1 F1NL0 MNW‐11‐D1‐7 7/11/2005 8:27 PDB GW µg/L 3.4 = 0.5 U 0.17 LJ 20 = 0.15 LJMNW‐11 (D1) D1 F1NK9DL MNW‐11‐D1‐2 7/11/2005 8:25 PDB GW µg/L 25 =MNW‐11 (D1) D1 F1NK9 MNW‐11‐D1‐2 7/11/2005 8:25 PDB GW µg/L 4.4 = 0.5 U 0.22 LJ 0.12 LJMNW‐11 (D1) D1 F1DG3 MNW‐11‐D1‐17 4/19/2005 10:14 PDB GW µg/L 2.9 = 0.5 U 0.12 LJ 14 = 0.5 UMNW‐11 (D1) D1 F1DG2 MNW‐11‐D1‐12 4/19/2005 10:11 PDB GW µg/L 3 = 0.5 U 0.13 LJ 14 = 0.5 UMNW‐11 (D1) D1 F1DG1 MNW‐11‐D1‐7 4/19/2005 10:09 PDB GW µg/L 3.1 = 0.5 U 0.12 LJ 14 = 0.5 UMNW‐11 (D1) D1 F1DG0 MNW‐11‐D1‐2 4/19/2005 10:06 PDB GW µg/L 2.8 = 0.5 U 0.13 LJ 14 = 0.5 U
MNW‐11 (D2) 5/10/2020 0:00 unknownMNW‐11 (D2) D2 F6PB5 MNW‐11‐D2‐2 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F5G12 MNW‐11‐D2‐17 2/27/2012 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.099 LJ 0.5 UMNW‐11 (D2) D2 F5G11 MNW‐11‐D2‐12 2/27/2012 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.12 LJ 0.5 UMNW‐11 (D2) D2 F5G14 MNW‐11‐D2‐7 2/27/2012 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.097 LJ 0.5 UMNW‐11 (D2) D2 F5G13 MNW‐11‐D2‐2 2/27/2012 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.15 LJ 0.5 UMNW‐11 (D2) D2 F4EB0 MNW‐11‐D2‐17‐Q311 8/22/2011 13:10 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 F4EA9 MNW‐11‐D2‐12‐Q311 8/22/2011 13:08 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 F4EB2 MNW‐11‐D2‐7‐Q311 8/22/2011 13:06 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 F4EB1 MNW‐11‐D2‐2‐Q311 8/22/2011 13:05 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐11 (D2) D2 MNW‐11‐D2‐17‐Q111 MNW‐11‐D2‐17 2/16/2011 10:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 MNW‐11‐D2‐12‐Q111 MNW‐11‐D2‐12 2/16/2011 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 MNW‐11‐D2‐7‐Q111 MNW‐11‐D2‐7 2/16/2011 10:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 26 OF 64
011514
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐11 (D2) D2 MNW‐11‐D2‐2‐Q111 MNW‐11‐D2‐2 2/16/2011 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1NL6 MNW‐11‐D2‐17 7/11/2005 8:52 PDB GW µg/L 0.5 U 0.22 LJ 0.5 U 0.14 LJ 0.5 UMNW‐11 (D2) D2 F1NL5 MNW‐11‐D2‐12 7/11/2005 8:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1NL4 MNW‐11‐D2‐7 7/11/2005 8:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1NL3 MNW‐11‐D2‐2 7/11/2005 8:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.13 LJ 0.5 UMNW‐11 (D2) D2 F1DG7 MNW‐11‐D2‐17 4/19/2005 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1DG6 MNW‐11‐D2‐12 4/19/2005 10:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1DG5 MNW‐11‐D2‐7 4/19/2005 10:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (D2) D2 F1DG4 MNW‐11‐D2‐2 4/19/2005 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐11 (I1) 5/10/2020 0:00 unknownMNW‐11 (I1) I1 F6PB6 MNW‐11‐I1‐5 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.33 LJ 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐5‐Q111 MNW‐11‐I1‐5 2/16/2011 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐7‐Q209 MNW‐11‐I1‐7 4/20/2009 13:05 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.7 = 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐7‐Q408 MNW‐11‐I1‐7 10/6/2008 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐11 (I1) I1 F2RR9 MNW‐11‐I1‐7 4/14/2008 0:00 PDB GW µg/L 0.37 LJ 0.5 U 0.5 U 0.88 = 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1‐7‐Q407 MNW‐11‐I1‐7 10/1/2007 9:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 UMNW‐11 (I1) I1 MNW‐11‐I1_070219 MNW‐11‐I1‐7 2/19/2007 14:19 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.7 JL 0.5 UJMNW‐11 (I1) I1 F2647 MNW‐11‐I1‐7 8/29/2006 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I1) I1 F1YM7 MNW‐11‐I1‐7 2/6/2006 9:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.66 = 0.5 UMNW‐11 (I1) I1 F1NK7 MNW‐11‐I1‐12 7/11/2005 9:02 PDB GW µg/L 0.27 LJ 0.5 U 0.5 U 0.59 = 0.5 UMNW‐11 (I1) I1 F1NK6 MNW‐11‐I1‐7 7/11/2005 9:00 PDB GW µg/L 0.31 LJ 0.5 U 0.5 U 0.86 = 0.5 UMNW‐11 (I1) I1 F1NK5 MNW‐11‐I1‐2 7/11/2005 8:58 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.77 = 0.5 UMNW‐11 (I1) I1 F1DF6 MNW‐11‐I1‐12 4/19/2005 9:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.43 LJ 0.5 UMNW‐11 (I1) I1 F1DF4 MNW‐11‐I1‐7 4/19/2005 9:35 PDB GW µg/L 0.23 LJ 0.5 U 0.5 U 0.63 = 0.5 UMNW‐11 (I1) I1 F1DF3 MNW‐11‐I1‐2 4/19/2005 9:32 PDB GW µg/L 0.23 LJ 0.5 U 0.5 U 0.64 = 0.5 U
MNW‐11 (I2) 5/10/2020 0:00 unknownMNW‐11 (I2) I2 F6PB7 MNW‐11‐I2‐8 2/19/2013 0:00 PDB GW µg/L 0.55 = 0.5 U 0.23 LJ 0.63 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐8‐Q111 MNW‐11‐I2‐8 2/16/2011 10:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐FD‐Q209 MNW‐11‐I2‐12‐FD 4/20/2009 13:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐Q209 MNW‐11‐I2‐12 4/20/2009 13:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐Q408 MNW‐11‐I2‐12 10/6/2008 9:42 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.7 = 0.5 UMNW‐11 (I2) I2 F2RS0 MNW‐11‐I2‐12 4/14/2008 0:00 PDB GW µg/L 0.79 = 0.5 U 0.49 LJ 0.92 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2‐12‐Q407 MNW‐11‐I2‐12 10/1/2007 9:13 PDB GW µg/L 0.8 = 0.5 U 0.6 = 1.1 = 0.5 UMNW‐11 (I2) I2 MNW‐11‐I2_070219 MNW‐11‐I2‐12 2/19/2007 14:50 PDB GW µg/L 0.9 JL 0.5 UJ 0.7 JL 1.4 JL 0.5 UJMNW‐11 (I2) I2 F2648 MNW‐11‐I2‐12 8/29/2006 10:10 PDB GW µg/L 0.69 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐11 (I2) I2 F1YN0 MNW‐11‐I2‐12 2/6/2006 9:42 PDB GW µg/L 1.2 = 0.5 U 0.5 U 3.5 = 0.5 UMNW‐11 (I2) I2 F1YM8 MNW‐11‐I2‐2 2/6/2006 9:40 PDB GW µg/L 0.68 = 0.5 U 0.5 U 2 = 0.5 UMNW‐11 (I2) I2 F1NK8 MNW‐11‐I2‐12 7/11/2005 9:35 PDB GW µg/L 1.4 = 0.5 U 0.5 U 3.7 = 0.5 UMNW‐11 (I2) I2 F1NK3 MNW‐11‐I2‐7 7/11/2005 9:31 PDB GW µg/L 1.4 = 0.5 U 0.5 U 3.8 = 0.5 UMNW‐11 (I2) I2 F1NK2 MNW‐11‐I2‐2 7/11/2005 9:30 PDB GW µg/L 1 = 0.5 U 0.5 U 2.3 = 0.5 UMNW‐11 (I2) I2 F1P97 MNW‐11‐I2‐17 7/11/2005 9:27 PDB GW µg/L 1.3 = 0.5 U 0.5 U 3.7 = 0.5 UMNW‐11 (I2) I2 F1DF9 MNW‐11‐I2‐12 4/19/2005 9:58 PDB GW µg/L 0.96 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐11 (I2) I2 F1DF8 MNW‐11‐I2‐7 4/19/2005 9:55 PDB GW µg/L 0.97 = 0.5 U 0.05 LJ 3 = 0.5 UMNW‐11 (I2) I2 F1DF7 MNW‐11‐I2‐2 4/19/2005 9:53 PDB GW µg/L 0.64 = 0.5 U 0.5 U 1.8 = 0.5 U
MNW‐12 (D1) 5/10/2020 0:00 unknownMNW‐12 (D1) D1 MNW‐12‐D1‐12‐022014 MNW‐12‐D1‐12 2/17/2014 12:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 27 OF 64
011515
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐12 (D1) D1 F6PB8 MNW‐12‐D1‐12 2/19/2013 0:00 PDB GW µg/L 0.58 = 0.5 U 0.5 U 1.1 = 0.5 UMNW‐12 (D1) D1 F6PB9 MNW‐12‐D1‐12‐FD 2/19/2013 0:00 PDB GW µg/L 0.64 = 0.5 U 0.5 U 1.2 = 0.5 UMNW‐12 (D1) D1 F5G15 MNW‐12‐D1‐12 2/27/2012 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q111‐FD MNW‐12‐D1‐12 2/16/2011 9:25 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q111 MNW‐12‐D1‐12 2/16/2011 9:20 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.4 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12_100202 MNW‐12‐D1‐12 2/2/2010 10:10 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.3 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q408 MNW‐12‐D1‐12 10/6/2008 8:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.6 = 0.5 UMNW‐12 (D1) D1 F2RS7 MNW‐12‐D1‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12‐Q407 MNW‐12‐D1‐12 10/1/2007 10:00 PDB GW µg/L 0.9 = 0.5 U 0.5 U 3.2 = 0.5 UMNW‐12 (D1) D1 MNW‐12‐D1‐12_070219 MNW‐12‐D1‐12 2/19/2007 14:58 PDB GW µg/L 0.9 JL 0.5 UJ 0.5 UJ 3.1 JL 0.5 UJMNW‐12 (D1) D1 F2650 MNW‐12‐D1‐12 8/29/2006 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.2 J 0.5 UMNW‐12 (D1) D1 F1YN8 MNW‐12‐D1‐17 2/6/2006 11:50 PDB GW µg/L 0.71 = 0.5 U 0.5 U 2.8 = 0.5 UMNW‐12 (D1) D1 F1YN7 MNW‐12‐D1‐12 2/6/2006 11:48 PDB GW µg/L 0.71 = 0.5 U 0.5 U 2.9 = 0.5 UMNW‐12 (D1) D1 F1YN6 MNW‐12‐D1‐7 2/6/2006 11:46 PDB GW µg/L 0.64 = 0.5 U 0.5 U 2.5 = 0.5 UMNW‐12 (D1) D1 F1NM7 MNW‐12‐D1‐17 7/11/2005 10:56 PDB GW µg/L 0.52 = 0.5 U 0.5 U 2.9 J 0.5 UMNW‐12 (D1) D1 F1NM5 MNW‐12‐D1‐12 7/11/2005 10:53 PDB GW µg/L 0.46 LJ 0.5 U 0.5 U 3.1 = 0.5 UMNW‐12 (D1) D1 F1NM4 MNW‐12‐D1‐7 7/11/2005 10:51 PDB GW µg/L 0.73 = 0.5 U 0.5 U 2.4 = 0.5 UMNW‐12 (D1) D1 F1NM3 MNW‐12‐D1‐2 7/11/2005 10:50 PDB GW µg/L 0.76 = 0.5 U 0.5 U 1.8 = 0.1 LJMNW‐12 (D1) D1 F1DH8 MNW‐12‐D1‐17 4/18/2005 15:11 PDB GW µg/L 0.48 LJ 0.5 U 0.5 U 1.5 J 0.5 UMNW‐12 (D1) D1 F1DH6 MNW‐12‐D1‐12 4/18/2005 15:04 PDB GW µg/L 0.4 LJ 0.5 U 0.5 U 1.5 = 0.5 UMNW‐12 (D1) D1 F1DH5 MNW‐12‐D1‐7 4/18/2005 14:57 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 1.5 = 0.5 UMNW‐12 (D1) D1 F1DH4 MNW‐12‐D1‐2 4/18/2005 14:54 PDB GW µg/L 0.41 LJ 0.5 U 0.5 U 1.4 = 0.5 U
MNW‐12 (D2) 5/10/2020 0:00 unknownMNW‐12 (D2) D2 F6PC0 MNW‐12‐D2‐7 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G20 MNW‐12‐D2‐7 2/27/2012 8:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G19 MNW‐12‐D2‐2 2/27/2012 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G18 MNW‐12‐D2‐17 2/27/2012 8:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G17 MNW‐12‐D2‐12‐FD 2/27/2012 8:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F5G16 MNW‐12‐D2‐12 2/27/2012 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F4EB4 MNW‐12‐D2‐17‐Q311 8/22/2011 9:49 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 F4EB3 MNW‐12‐D2‐12‐Q311 8/22/2011 9:47 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 F4EB6 MNW‐12‐D2‐7‐Q311 8/22/2011 9:46 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 F4EB5 MNW‐12‐D2‐2‐Q311 8/22/2011 9:45 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (D2) D2 MNW‐12‐D2‐17‐Q111 MNW‐12‐D2‐17 2/16/2011 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 MNW‐12‐D2‐12‐Q111 MNW‐12‐D2‐12 2/16/2011 9:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 MNW‐12‐D1‐7‐Q111 MNW‐12‐D2‐7 2/16/2011 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 MNW‐12‐D2‐2‐Q111 MNW‐12‐D2‐2 2/16/2011 9:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1NN1 MNW‐12‐D2‐17 7/11/2005 11:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1NN0 MNW‐12‐D2‐12 7/11/2005 11:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1NM9 MNW‐12‐D2‐7 7/11/2005 11:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1NM8 MNW‐12‐D2‐2 7/11/2005 11:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1DJ2 MNW‐12‐D2‐17 4/18/2005 15:31 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 0.5 U 0.16 LJMNW‐12 (D2) D2 F1DJ1 MNW‐12‐D2‐12 4/18/2005 15:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1DJ0 MNW‐12‐D2‐7 4/18/2005 15:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (D2) D2 F1DH9 MNW‐12‐D2‐2 4/18/2005 15:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐12 (I1) 5/10/2020 0:00 unknown
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 28 OF 64
011516
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐12 (I1) I1 F6PC1 MNW‐12‐I1‐8 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F5G23 MNW‐12‐I1‐8 2/27/2012 8:52 PDB GW µg/L 0.49 LJ 0.5 U 0.5 U 0.75 = 0.5 UMNW‐12 (I1) I1 F5G22 MNW‐12‐I1‐5 2/27/2012 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F5G21 MNW‐12‐I1‐2 2/27/2012 8:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F4EB9 MNW‐12‐I1‐12‐Q311 8/22/2011 10:07 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 F4EB8 MNW‐12‐I1‐7‐FD‐Q311 8/22/2011 10:06 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 F4EB7 MNW‐12‐I1‐7‐Q311 8/22/2011 10:05 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 F4ED3 MNW‐12‐I1‐2‐Q311 8/22/2011 10:04 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐12 (I1) I1 MNW‐12‐I1‐8‐Q111 MNW‐12‐I1‐12 2/16/2011 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 MNW‐12‐I1‐5‐Q111 MNW‐12‐I1‐7 2/16/2011 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 MNW‐12‐I1‐2‐Q111 MNW‐12‐I1‐2 2/16/2011 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1NL9 MNW‐12‐I1‐12 7/11/2005 10:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1NL8 MNW‐12‐I1‐7 7/11/2005 10:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1NL7 MNW‐12‐I1‐2 7/11/2005 10:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1DH0 MNW‐12‐I1‐12 4/18/2005 14:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1DG9 MNW‐12‐I1‐7 4/18/2005 14:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I1) I1 F1DG8 MNW‐12‐I1‐2 4/18/2005 14:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐12 (I2) 5/10/2020 0:00 unknownMNW‐12 (I2) I2 F6PC2 MNW‐12‐I2‐5 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐5‐Q111 MNW‐12‐I2‐5 2/16/2011 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐7‐Q209 MNW‐12‐I2‐7 4/20/2009 14:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐7‐Q408 MNW‐12‐I2‐7 10/6/2008 8:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F2RS6 MNW‐12‐I2‐7 4/14/2008 0:00 PDB GW µg/L 0.8 = 0.5 U 0.5 U 2.3 = 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2‐7‐Q407 MNW‐12‐I2‐7 10/1/2007 9:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 MNW‐12‐I2_070219 MNW‐12‐I2‐7 2/19/2007 14:49 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐12 (I2) I2 F2651 MNW‐12‐I2‐7 8/29/2006 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1YN5 MNW‐12‐I2‐7 2/6/2006 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1NM2 MNW‐12‐I2‐12 7/11/2005 10:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1NM1 MNW‐12‐I2‐7 7/11/2005 10:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1NM0 MNW‐12‐I2‐2 7/11/2005 10:39 PDB GW µg/L 0.5 U 0.13 LJ 0.5 U 0.5 U 0.11 LJMNW‐12 (I2) I2 F1DH3 MNW‐12‐I2‐12 4/18/2005 14:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐12 (I2) I2 F1DH2 MNW‐12‐I2‐7 4/18/2005 14:42 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 UMNW‐12 (I2) I2 F1DH1 MNW‐12‐I2‐2 4/18/2005 14:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐13 (D1) 5/10/2020 0:00 unknownMNW‐13 (D1) D1 MNW‐13‐D1‐7‐022014 MNW‐13‐D1‐7 2/18/2014 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 UMNW‐13 (D1) D1 F6PC3 MNW‐13‐D1‐7 2/12/2013 0:00 PDB GW µg/L 0.34 LJ 0.32 LJ 0.5 U 1.1 = 0.5 UMNW‐13 (D1) D1 F5G24 MNW‐13‐D1‐7 2/28/2012 13:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.4 = 0.5 UMNW‐13 (D1) D1 F3S12 MNW‐13‐D1‐7 2/15/2011 8:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1‐12_100201 MNW‐13‐D1‐12 2/1/2010 11:08 PDB GW µg/L 0.5 = 0.8 = 0.5 U 1.9 = 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1‐7‐Q209 MNW‐13‐D1‐7 4/21/2009 12:35 PDB GW µg/L 0.5 J 0.9 J 0.5 UJ 2.0 J 0.5 UJMNW‐13 (D1) D1 MNW‐13‐D1‐7‐Q408 MNW‐13‐D1‐7 10/6/2008 14:12 PDB GW µg/L 0.5 = 0.7 = 0.5 U 2 = 0.5 UMNW‐13 (D1) D1 F2RS8 MNW‐13‐D1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2.6 = 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1‐7‐Q407 MNW‐13‐D1‐7 10/2/2007 11:25 PDB GW µg/L 0.6 = 1 = 0.5 U 2.5 = 0.5 UMNW‐13 (D1) D1 MNW‐13‐D1_070219 MNW‐13‐D1‐7 2/19/2007 11:22 PDB GW µg/L 0.5 UJ 0.6 JL 0.5 UJ 1.8 JL 0.5 UJMNW‐13 (D1) D1 F2652 MNW‐13‐D1‐7 8/29/2006 7:20 PDB GW µg/L 0.5 U 0.58 = 0.5 U 1.8 = 0.5 UMNW‐13 (D1) D1 F1YT0 MNW‐13‐D1‐7 2/6/2006 9:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 29 OF 64
011517
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐13 (D1) D1 F1P22 MNW‐13‐D1‐17 7/11/2005 8:44 PDB GW µg/L 0.43 LJ 1 = 0.18 LJ 3.4 = 0.5 UMNW‐13 (D1) D1 F1P20 MNW‐13‐D1‐12 7/11/2005 8:42 PDB GW µg/L 0.36 LJ 0.92 = 0.12 LJ 2.7 = 0.5 UMNW‐13 (D1) D1 F1P19 MNW‐13‐D1‐7 7/11/2005 8:38 PDB GW µg/L 0.39 LJ 0.7 = 0.18 LJ 2.9 = 0.5 UMNW‐13 (D1) D1 F1DX0 MNW‐13‐D1‐17 4/18/2005 11:00 PDB GW µg/L 0.76 = 1.2 = 0.5 U 3.6 = 0.5 UMNW‐13 (D1) D1 F1DW9 MNW‐13‐D1‐12 4/18/2005 10:58 PDB GW µg/L 0.79 = 1.1 = 0.17 LJ 3.6 = 0.5 UMNW‐13 (D1) D1 F1DW8 MNW‐13‐D1‐7 4/18/2005 10:56 PDB GW µg/L 0.67 = 0.74 = 0.22 LJ 3.1 = 0.5 U
MNW‐13 (D2) 5/10/2020 0:00 unknownMNW‐13 (D2) D2 MNW‐13‐D2‐7‐022014 MNW‐13‐D2‐7 2/18/2014 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7‐022014‐FD MNW‐13‐D2‐7‐FD 2/18/2014 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F6PC4 MNW‐13‐D2‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F6PC5 MNW‐13‐D2‐7‐FD 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F5G25 MNW‐13‐D2‐7 2/28/2012 14:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F3S14 MNW‐13‐D2‐7 2/15/2011 10:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F3S13 MNW‐13‐D2‐7 2/15/2011 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7_100201 MNW‐13‐D2‐7 2/1/2010 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7‐Q209 MNW‐13‐D2‐7 4/21/2009 12:46 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D2) D2 MNW‐13‐D2‐7‐Q408 MNW‐13‐D2‐7 10/6/2008 13:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F2RS9 MNW‐13‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2‐7‐Q407 MNW‐13‐D2‐7 10/2/2007 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 MNW‐13‐D2_070219 MNW‐13‐D2‐7 2/19/2007 11:40 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D2) D2 F2653 MNW‐13‐D2‐7 8/29/2006 7:40 PDB GW µg/L 0.68 = 0.5 U 0.5 U 1.5 = 0.5 UMNW‐13 (D2) D2 F1YT1 MNW‐13‐D2‐7 2/6/2006 9:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P26 MNW‐13‐D2‐17 7/11/2005 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P25 MNW‐13‐D2‐12 7/11/2005 9:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P24 MNW‐13‐D2‐7 7/11/2005 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1P23 MNW‐13‐D2‐2 7/11/2005 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1DX4 MNW‐13‐D2‐17 4/18/2005 9:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1DX3 MNW‐13‐D2‐12 4/18/2005 9:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1DX2 MNW‐13‐D2‐7 4/18/2005 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D2) D2 F1DX1 MNW‐13‐D2‐2 4/18/2005 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐13 (D3) 5/10/2020 0:00 unknownMNW‐13 (D3) D3 MNW‐13‐D3‐7‐022014 MNW‐13‐D3‐7 2/18/2014 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F6PC6 MNW‐13‐D3‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F5G26 MNW‐13‐D3‐7 2/28/2012 14:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F3S15 MNW‐13‐D3‐7 2/15/2011 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3‐7_100201 MNW‐13‐D3‐7 2/1/2010 10:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3‐7‐Q209 MNW‐13‐D3‐7 4/21/2009 13:07 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D3) D3 MNW‐13‐D3‐7‐Q408 MNW‐13‐D3‐7 10/6/2008 14:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F2RT0 MNW‐13‐D3‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3‐7‐Q407 MNW‐13‐D3‐7 10/2/2007 11:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 MNW‐13‐D3_070219 MNW‐13‐D3‐7 2/19/2007 11:55 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D3) D3 F2654 MNW‐13‐D3‐7 8/29/2006 8:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UJMNW‐13 (D3) D3 F1YT2 MNW‐13‐D3‐7 2/6/2006 9:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1P30 MNW‐13‐D3‐17 7/11/2005 9:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1P28 MNW‐13‐D3‐7 7/11/2005 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1P29 MNW‐13‐D3‐12 7/11/2005 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 30 OF 64
011518
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐13 (D3) D3 F1P27 MNW‐13‐D3‐2 7/11/2005 9:18 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX8 MNW‐13‐D3‐17 4/18/2005 10:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX7 MNW‐13‐D3‐12 4/18/2005 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX6 MNW‐13‐D3‐7 4/18/2005 10:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D3) D3 F1DX5 MNW‐13‐D3‐2 4/18/2005 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐13 (D4) 5/10/2020 0:00 unknownMNW‐13 (D4) D4 MNW‐13‐D4‐7‐FD‐Q209 MNW‐13‐D4‐7‐FD 4/21/2009 13:06 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D4) D4 MNW‐13‐D4‐7‐Q209 MNW‐13‐D4‐7 4/21/2009 13:05 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D4) D4 MNW‐13‐D4‐7‐Q408 MNW‐13‐D4‐7 10/6/2008 14:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F2RT1 MNW‐13‐D4‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 MNW‐13‐D4‐7‐Q407 MNW‐13‐D4‐7 10/2/2007 12:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 MNW‐13‐D4_070219 MNW‐13‐D4‐7 2/19/2007 12:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐13 (D4) D4 F2655 MNW‐13‐D4‐7 8/29/2006 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1YT4 MNW‐13‐D4‐12 2/6/2006 9:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1YT3 MNW‐13‐D4‐7 2/6/2006 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P33 MNW‐13‐D4‐12 7/11/2005 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P34 MNW‐13‐D4‐17 7/11/2005 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P32 MNW‐13‐D4‐7 7/11/2005 9:46 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1P31 MNW‐13‐D4‐2 7/11/2005 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1DY2 MNW‐13‐D4‐17 4/18/2005 9:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1DY1 MNW‐13‐D4‐12 4/18/2005 9:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1DY0 MNW‐13‐D4‐7 4/18/2005 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐13 (D4) D4 F1DX9 MNW‐13‐D4‐2 4/18/2005 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐14 (D1) 5/10/2020 0:00 unknownMNW‐14 (D1) D1 MNW‐14‐D1‐7‐022014 MNW‐14‐D1‐7 2/17/2014 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐0813 MNW‐14‐D1‐7 8/12/2013 9:29 PDB WG µg/L 0.5 U 0.5 U 0.5 U 1.7 = 0.5 UMNW‐14 (D1) D1 F6PC7 MNW‐14‐D1‐7 2/13/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.86 = 0.5 UMNW‐14 (D1) D1 F6CA5 MNW‐14‐D1‐7 8/20/2012 10:05 PDB GW µg/L 0.16 LJ 0.5 U 0.5 U 0.74 = 0.5 UMNW‐14 (D1) D1 F5G83 MNW‐14‐D1‐7 2/27/2012 9:53 PDB GW µg/L 0.22 LJ 0.5 U 0.5 U 1.8 = 0.5 UMNW‐14 (D1) D1 F4EC0 MNW‐14‐D1‐7‐Q311 8/22/2011 12:25 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐Q111 MNW‐14‐D1‐7 2/14/2011 11:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐Q408 MNW‐14‐D1‐7 10/6/2008 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F2RY4 MNW‐14‐D1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1‐7‐Q407 MNW‐14‐D1‐7 10/2/2007 9:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 MNW‐14‐D1_070219 MNW‐14‐D1‐7 2/19/2007 9:10 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐14 (D1) D1 F2657 MNW‐14‐D1‐7 8/29/2006 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1YQ3 MNW‐14‐D1‐7 2/6/2006 13:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP5 MNW‐14‐D1‐17 7/12/2005 9:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP4 MNW‐14‐D1‐12 7/12/2005 9:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP3 MNW‐14‐D1‐7 7/12/2005 9:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1NP1 MNW‐14‐D1‐2 7/12/2005 9:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK6 MNW‐14‐D1‐17 4/18/2005 11:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK5 MNW‐14‐D1‐12 4/18/2005 11:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK4 MNW‐14‐D1‐7 4/18/2005 11:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D1) D1 F1DK2 MNW‐14‐D1‐2 4/18/2005 11:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐14 (D2) 5/10/2020 0:00 unknown
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 31 OF 64
011519
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐14 (D2) D2 MNW‐14‐D2‐17‐Q209 MNW‐14‐D2‐17 4/20/2009 11:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐2‐Q209 MNW‐14‐D2‐2 4/20/2009 11:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐17‐Q408 MNW‐14‐D2‐17 10/6/2008 9:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐2‐Q408 MNW‐14‐D2‐2 10/6/2008 9:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 F2RY6 MNW‐14‐D2‐17 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.29 LJ 0.19 LJ 0.5 UMNW‐14 (D2) D2 F2RY5 MNW‐14‐D2‐2 4/14/2008 0:00 PDB GW µg/L 0.18 LJ 0.5 U 0.3 LJ 0.19 LJ 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐17‐Q407 MNW‐14‐D2‐17 10/2/2007 9:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐2‐Q407 MNW‐14‐D2‐2 10/2/2007 9:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 MNW‐14‐D2‐17_070219 MNW‐14‐D2‐17 2/19/2007 9:25 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐14 (D2) D2 MNW‐14‐D2‐2_070219 MNW‐14‐D2‐2 2/19/2007 9:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐14 (D2) D2 F2658 MNW‐14‐D2‐17 8/29/2006 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 F2659 MNW‐14‐D2‐2 8/29/2006 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐14 (D2) D2 F1YQ5 MNW‐14‐D2‐17 2/6/2006 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.74 = 0.5 UMNW‐14 (D2) D2 F1YQ4 MNW‐14‐D2‐2 2/6/2006 13:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.74 = 0.5 UMNW‐14 (D2) D2 F1NP9 MNW‐14‐D2‐17 7/12/2005 9:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.92 = 0.5 UMNW‐14 (D2) D2 F1NP8 MNW‐14‐D2‐12 7/12/2005 9:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.75 = 0.5 UMNW‐14 (D2) D2 F1NP7 MNW‐14‐D2‐7 7/12/2005 9:51 PDB GW µg/L 0.11 LJ 0.5 U 0.5 U 0.73 = 0.5 UMNW‐14 (D2) D2 F1NP6 MNW‐14‐D2‐2 7/12/2005 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.82 = 0.5 UMNW‐14 (D2) D2 F1DL0 MNW‐14‐D2‐17 4/18/2005 11:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.67 = 0.5 UMNW‐14 (D2) D2 F1DK9 MNW‐14‐D2‐12 4/18/2005 11:49 PDB GW µg/L 0.12 LJ 0.5 U 0.5 U 0.67 = 0.5 UMNW‐14 (D2) D2 F1DK8 MNW‐14‐D2‐7 4/18/2005 11:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.66 = 0.5 UMNW‐14 (D2) D2 F1DK7 MNW‐14‐D2‐2 4/18/2005 11:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.78 = 0.5 U
MNW‐14 (I2) 5/10/2020 0:00 unknownMNW‐14 (I2) I2 MNW‐14‐I2‐8‐022014 MNW‐14‐I2‐8 2/17/2014 10:49 PDB GW µg/L 7.7 = 0.5 U 1.1 = 38.2 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐022014 MNW‐14‐I2‐2 2/17/2014 10:44 PDB GW µg/L 7.6 = 0.5 U 1.1 = 32.4 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐0813 MNW‐14‐I2‐2 8/12/2013 9:22 PDB WG µg/L 8.4 = 0.5 U 1.1 = 36.8 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐0813 MNW‐14‐I2‐8 8/12/2013 9:20 PDB WG µg/L 7.7 = 0.5 U 0.9 = 42.8 = 0.5 UMNW‐14 (I2) I2 F6PC8 MNW‐14‐I2‐2 2/13/2013 0:00 PDB GW µg/L 9.2 = 0.5 U 0.99 = 33 = 0.5 UMNW‐14 (I2) I2 F6PC9 MNW‐14‐I2‐8 2/13/2013 0:00 PDB GW µg/L 8.8 = 0.5 U 0.85 = 39 = 0.5 UMNW‐14 (I2) I2 F6CA7 MNW‐14‐I2‐8 8/20/2012 10:21 PDB GW µg/L 7.6 = 0.16 LJ 0.70 LJ 48 = 2.5 UMNW‐14 (I2) I2 F6CA6 MNW‐14‐I2‐2 8/20/2012 10:18 PDB GW µg/L 8.1 = 2.5 U 0.69 LJ 46 = 2.5 UMNW‐14 (I2) I2 F5G85DL MNW‐14‐I2‐8 2/27/2012 9:40 PDB GW µg/L 35 =MNW‐14 (I2) I2 F5G85 MNW‐14‐I2‐8 2/27/2012 9:40 PDB GW µg/L 7.8 = 0.5 U 0.93 = 0.5 UMNW‐14 (I2) I2 F5G84DL MNW‐14‐I2‐2 2/27/2012 9:38 PDB GW µg/L 39 =MNW‐14 (I2) I2 F5G84 MNW‐14‐I2‐2 2/27/2012 9:38 PDB GW µg/L 8.6 = 0.5 U 3 = 0.5 UMNW‐14 (I2) I2 F4EC2 MNW‐14‐I2‐8‐Q311 8/22/2011 12:40 PDB GW µg/L 9.7 = 5.0 U 5.0 U 51 = 2.0 UMNW‐14 (I2) I2 F4EC1 MNW‐14‐I2‐2‐Q311 8/22/2011 12:35 PDB GW µg/L 11 = 5.0 U 1.3 LJ 44 = 2.0 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q111 MNW‐14‐I2‐8 2/14/2011 11:07 PDB GW µg/L 6.5 = 0.5 U 2 = 26.2 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q111 MNW‐14‐I2‐2 2/14/2011 11:06 PDB GW µg/L 7.4 = 0.5 U 0.8 = 32.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q310 MNW‐14‐I2‐8‐Q310 9/7/2010 13:35 PDB GW µg/L 8.2 = 0.5 U 1.2 = 30.0 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q310 MNW‐14‐I2‐2‐Q310 9/7/2010 13:30 PDB GW µg/L 8.8 = 0.5 U 1.1 = 32.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8_100201 MNW‐14‐I2‐8 2/1/2010 11:18 PDB GW µg/L 8.1 = 0.5 U 0.6 = 34.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2_100201 MNW‐14‐I2‐2 2/1/2010 11:15 PDB GW µg/L 8.8 = 0.5 U 0.7 = 31.7 = 0.5 UMNW‐14 (I2) I2 F3B79 MNW‐14‐I2‐8 10/26/2009 13:03 PDB GW µg/L 9.1 = 0.5 U 0.66 = 32 = 0.5 UMNW‐14 (I2) I2 F3B78 MNW‐14‐I2‐2 10/26/2009 13:00 PDB GW µg/L 7.8 = 0.5 U 0.61 = 37 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q209 MNW‐14‐I2‐8 4/20/2009 11:47 PDB GW µg/L 9.2 = 0.5 U 0.9 = 36.9 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 32 OF 64
011520
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐14 (I2) I2 MNW‐14‐I2‐2‐FD‐Q209 MNW‐14‐I2‐2‐FD 4/20/2009 11:45 PDB GW µg/L 8.0 = 0.5 U 0.7 = 30.7 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q209 MNW‐14‐I2‐2 4/20/2009 11:44 PDB GW µg/L 8.1 = 0.5 U 0.8 = 32.6 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q408 MNW‐14‐I2‐8 10/6/2008 8:43 PDB GW µg/L 9.6 = 0.5 U 0.7 = 32.5 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q408 MNW‐14‐I2‐2 10/6/2008 8:36 PDB GW µg/L 8.2 = 0.5 U 0.7 = 29.7 = 0.5 UMNW‐14 (I2) I2 F2RY3 MNW‐14‐I2‐8 4/14/2008 0:00 PDB GW µg/L 6.9 = 0.5 U 0.74 = 20 = 0.5 UMNW‐14 (I2) I2 F2RZ2 MNW‐14‐I2‐2 4/14/2008 0:00 PDB GW µg/L 8.7 = 0.5 U 0.82 = 21 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐8‐Q407 MNW‐14‐I2‐8 10/2/2007 9:24 PDB GW µg/L 7.2 = 0.5 U 0.7 = 29.1 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2‐Q407 MNW‐14‐I2‐2 10/2/2007 9:20 PDB GW µg/L 6.6 = 0.5 U 0.7 = 25.2 = 0.5 UMNW‐14 (I2) I2 MNW‐14‐I2‐2_070219 MNW‐14‐I2‐2 2/19/2007 9:50 PDB GW µg/L 5.1 JL 0.5 UJ 0.7 JL 22.8 JL 0.5 UJMNW‐14 (I2) I2 MNW‐14‐I2‐8_070219 MNW‐14‐I2‐8 2/19/2007 9:45 PDB GW µg/L 5.9 JL 0.5 UJ 0.7 JL 26.5 JL 0.5 UJMNW‐14 (I2) I2 F2662 MNW‐14‐I2‐8 8/29/2006 8:40 PDB GW µg/L 2.8 = 0.5 U 0.5 U 15 = 0.5 UMNW‐14 (I2) I2 F2660 MNW‐14‐I2‐2 8/29/2006 8:37 PDB GW µg/L 3.1 = 0.5 U 0.5 U 17 = 0.5 UMNW‐14 (I2) I2 F1YQ2 MNW‐14‐I2‐8 2/6/2006 13:27 PDB GW µg/L 4.4 = 0.5 U 0.6 = 20 = 0.5 UMNW‐14 (I2) I2 F1YQ1 MNW‐14‐I2‐5 2/6/2006 13:25 PDB GW µg/L 4.1 = 0.5 U 0.71 = 16 = 0.5 UMNW‐14 (I2) I2 F1YP9 MNW‐14‐I2‐2 2/6/2006 13:18 PDB GW µg/L 4 = 0.5 U 0.59 = 17 = 0.5 UMNW‐14 (I2) I2 F1NN9 MNW‐14‐I2‐8 7/12/2005 10:07 PDB GW µg/L 5.4 = 0.5 U 0.71 = 23 = 0.1 LJMNW‐14 (I2) I2 F1NN8 MNW‐14‐I2‐5 7/12/2005 10:05 PDB GW µg/L 5.2 = 0.5 U 0.84 = 22 = 0.16 LJMNW‐14 (I2) I2 F1NN7 MNW‐14‐I2‐2 7/12/2005 10:03 PDB GW µg/L 4.7 = 0.8 U 0.62 LJ 24 = 0.8 UMNW‐14 (I2) I2 F1DK0 MNW‐14‐I2‐8 4/18/2005 11:03 PDB GW µg/L 3.5 J 0.5 U 0.43 LJ 11 J 0.5 UMNW‐14 (I2) I2 F1DJ9DL MNW‐14‐I2‐5 4/18/2005 10:57 PDB GW µg/L 16 =MNW‐14 (I2) I2 F1DJ9 MNW‐14‐I2‐5 4/18/2005 10:57 PDB GW µg/L 5.9 = 0.5 U 0.88 J 0.2 LJMNW‐14 (I2) I2 F1DJ8DL MNW‐14‐I2‐2 4/18/2005 10:50 PDB GW µg/L 25 =MNW‐14 (I2) I2 F1DJ8 MNW‐14‐I2‐2 4/18/2005 10:50 PDB GW µg/L 6.7 = 0.5 U 0.93 J 0.23 LJ
MNW‐15 (D1) 5/10/2020 0:00 unknownMNW‐15 (D1) D1 F6PD0 MNW‐15‐D1‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F5G28 MNW‐15‐D1‐7‐FD 2/28/2012 14:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F5G27 MNW‐15‐D1‐7 2/28/2012 13:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F3S16 MNW‐15‐D1‐7 2/15/2011 12:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7_100201 MNW‐15‐D1‐7 2/1/2010 7:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7‐Q209 MNW‐15‐D1‐7 4/20/2009 13:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7‐Q408 MNW‐15‐D1‐7 10/6/2008 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2RT3 MNW‐15‐D1‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐2‐Q407 MNW‐15‐D1‐2 10/1/2007 13:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐7‐Q407 MNW‐15‐D1‐7 10/1/2007 13:26 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐12‐Q407 MNW‐15‐D1‐12 10/1/2007 13:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐17‐Q407 MNW‐15‐D1‐17 10/1/2007 13:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 MNW‐15‐D1‐17_070219 MNW‐15‐D1‐17 2/19/2007 13:38 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 MNW‐15‐D1‐12_070219 MNW‐15‐D1‐12 2/19/2007 13:36 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 MNW‐15‐D1‐7_070219 MNW‐15‐D1‐7 2/19/2007 13:34 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 MNW‐15‐D1‐2_070219 MNW‐15‐D1‐2 2/19/2007 13:31 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D1) D1 F2664 MNW‐15‐D1‐17 8/29/2006 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2663 MNW‐15‐D1‐12 8/29/2006 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2666 MNW‐15‐D1‐7 8/29/2006 9:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F2665 MNW‐15‐D1‐2 8/29/2006 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F1YS1 MNW‐15‐D1‐17 2/7/2006 8:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F1YS0 MNW‐15‐D1‐12 2/7/2006 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 33 OF 64
011521
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐15 (D1) D1 F1YR9 MNW‐15‐D1‐7 2/7/2006 8:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D1) D1 F1YR8 MNW‐15‐D1‐2 2/7/2006 8:31 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐15 (D2) 5/10/2020 0:00 unknownMNW‐15 (D2) D2 F6PD1 MNW‐15‐D2‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F5G29 MNW‐15‐D2‐7 2/28/2012 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F3S17 MNW‐15‐D2‐7 2/15/2011 12:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐7‐Q209 MNW‐15‐D2‐7 4/20/2009 14:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐7‐Q408 MNW‐15‐D2‐7 10/6/2008 11:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2RT4 MNW‐15‐D2‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐2‐Q407 MNW‐15‐D2‐2 10/1/2007 13:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐7‐Q407 MNW‐15‐D2‐7 10/1/2007 13:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐12‐Q407 MNW‐15‐D2‐12 10/1/2007 13:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐17‐Q407 MNW‐15‐D2‐17 10/1/2007 13:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 MNW‐15‐D2‐17_070219 MNW‐15‐D2‐17 2/19/2007 14:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 MNW‐15‐D2‐12_070219 MNW‐15‐D2‐12 2/19/2007 13:57 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 MNW‐15‐D2‐7_070319 MNW‐15‐D2‐7 2/19/2007 13:54 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 MNW‐15‐D2‐2_070219 MNW‐15‐D2‐2 2/19/2007 13:52 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D2) D2 F2668 MNW‐15‐D2‐17 8/29/2006 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2667 MNW‐15‐D2‐12 8/29/2006 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2670 MNW‐15‐D2‐7 8/29/2006 9:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F2669 MNW‐15‐D2‐2 8/29/2006 9:50 PDB GW µg/L 0.5 UR 0.5 U 0.5 UR 0.5 U 0.5 URMNW‐15 (D2) D2 F1YS5 MNW‐15‐D2‐17 2/7/2006 9:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F1YS4 MNW‐15‐D2‐12 2/7/2006 8:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F1YS3 MNW‐15‐D2‐7 2/7/2006 8:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D2) D2 F1YS2 MNW‐15‐D2‐2 2/7/2006 8:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐15 (D3) 5/10/2020 0:00 unknownMNW‐15 (D3) D3 F6PD2 MNW‐15‐D3‐7 2/12/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F5G30 MNW‐15‐D3‐7 2/28/2012 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F3S18 MNW‐15‐D3‐7 2/15/2011 12:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7_100201 MNW‐15‐D3‐7 2/1/2010 8:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7‐Q209 MNW‐15‐D3‐7 4/20/2009 14:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7‐Q408 MNW‐15‐D3‐7 10/6/2008 11:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2RT5 MNW‐15‐D3‐7 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐2‐Q407 MNW‐15‐D3‐2 10/1/2007 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐7‐Q407 MNW‐15‐D3‐7 10/1/2007 14:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐12‐Q407 MNW‐15‐D3‐12 10/1/2007 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐17‐Q407 MNW‐15‐D3‐17 10/1/2007 14:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 MNW‐15‐D3‐17_070219 MNW‐15‐D3‐17 2/19/2007 14:20 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D3) D3 MNW‐15‐D3‐12_070219 MNW‐15‐D3‐12 2/19/2007 14:17 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D3) D3 MNW‐15‐D3‐7_070219 MNW‐15‐D3‐7 2/19/2007 14:15 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D3) D3 MNW‐15‐D3‐2_070219 MNW‐15‐D3‐2 2/19/2007 14:13 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJMNW‐15 (D3) D3 F2672 MNW‐15‐D3‐17 8/29/2006 10:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2671 MNW‐15‐D3‐12 8/29/2006 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2674 MNW‐15‐D3‐7 8/29/2006 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F2673 MNW‐15‐D3‐2 8/29/2006 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F1YS9 MNW‐15‐D3‐17 2/7/2006 9:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 34 OF 64
011522
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐15 (D3) D3 F1YS8 MNW‐15‐D3‐12 2/7/2006 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F1YS7 MNW‐15‐D3‐7 2/7/2006 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐15 (D3) D3 F1YS6 MNW‐15‐D3‐2 2/7/2006 9:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D1) 5/10/2020 0:00 unknownMNW‐16 (D1) D1 MNW‐16‐D1‐12‐022014 MNW‐16‐D1‐12 2/18/2014 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐17‐0813FD MNW‐16‐D1‐17FD 8/12/2013 9:15 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐17‐0813 MNW‐16‐D1‐17 8/12/2013 9:10 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐12‐0813 MNW‐16‐D1‐12 8/12/2013 9:05 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐7‐0813 MNW‐16‐D1‐7 8/12/2013 9:00 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 MNW‐16‐D1‐2‐0813 MNW‐16‐D1‐2 8/12/2013 8:45 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD6 MNW‐16‐D1‐17‐FD 2/12/2013 9:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD4 MNW‐16‐D1‐17 2/12/2013 9:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD3 MNW‐16‐D1‐12 2/12/2013 9:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD7 MNW‐16‐D1‐7 2/12/2013 9:24 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6PD5 MNW‐16‐D1‐2 2/12/2013 9:19 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE7 MNW‐16‐D1‐17 8/20/2012 10:21 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE6 MNW‐16‐D1‐12 8/20/2012 10:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE5 MNW‐16‐D1‐7 8/20/2012 10:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D1) D1 F6CE4 MNW‐16‐D1‐2 8/20/2012 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D2) 5/10/2020 0:00 unknownMNW‐16 (D2) D2 MNW‐16‐D2‐12‐022014 MNW‐16‐D2‐12 2/18/2014 8:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐17‐0813 MNW‐16‐D2‐17 8/12/2013 9:30 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐12‐0813 MNW‐16‐D2‐12 8/12/2013 9:25 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐7‐0813 MNW‐16‐D2‐7 8/12/2013 9:22 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 MNW‐16‐D2‐2‐0813 MNW‐16‐D2‐2 8/12/2013 9:20 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PD9 MNW‐16‐D2‐17 2/12/2013 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PD8 MNW‐16‐D2‐12 2/12/2013 9:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PE1 MNW‐16‐D2‐7 2/12/2013 9:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6PE0 MNW‐16‐D2‐2 2/12/2013 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CF1 MNW‐16‐D2‐17 8/20/2012 9:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CH8 MNW‐16‐D2‐12‐FD 8/20/2012 9:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CF0 MNW‐16‐D2‐12 8/20/2012 9:06 PDB GW µg/L 0.5 U 0.043 LJ 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CE9 MNW‐16‐D2‐7 8/20/2012 9:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D2) D2 F6CE8 MNW‐16‐D2‐2 8/20/2012 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D3) 5/10/2020 0:00 unknownMNW‐16 (D3) D3 MNW‐16‐D3‐12‐022014 MNW‐16‐D3‐12 2/18/2014 8:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐17‐0813 MNW‐16‐D3‐17 8/12/2013 10:00 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐12‐0813 MNW‐16‐D3‐12 8/12/2013 9:55 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐7‐0813 MNW‐16‐D3‐7 8/12/2013 9:50 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 MNW‐16‐D3‐2‐0813 MNW‐16‐D3‐2 8/12/2013 9:45 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE3 MNW‐16‐D3‐17 2/12/2013 10:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE2 MNW‐16‐D3‐12 2/12/2013 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE5 MNW‐16‐D3‐7 2/12/2013 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6PE4 MNW‐16‐D3‐2 2/12/2013 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF6 MNW‐16‐D3‐17 8/20/2012 9:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF5 MNW‐16‐D3‐12 8/20/2012 9:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 35 OF 64
011523
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodMNW‐16 (D3) D3 F6CF4 MNW‐16‐D3‐7‐FD 8/20/2012 9:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF3 MNW‐16‐D3‐7 8/20/2012 9:33 PDB GW µg/L 0.5 U 0.030 LJ 0.5 U 0.5 U 0.5 UMNW‐16 (D3) D3 F6CF2 MNW‐16‐D3‐2 8/20/2012 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
MNW‐16 (D4) 5/10/2020 0:00 unknownMNW‐16 (D4) D4 MNW‐16‐D4‐17‐0813FD MNW‐16‐D4‐17FD 8/12/2013 10:30 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐17‐0813 MNW‐16‐D4‐17 8/12/2013 10:25 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐12‐0813 MNW‐16‐D4‐12 8/12/2013 10:20 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐7‐0813 MNW‐16‐D4‐7 8/12/2013 10:15 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 MNW‐16‐D4‐2‐0813 MNW‐16‐D4‐2 8/12/2013 10:10 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE7 MNW‐16‐D4‐17 2/12/2013 11:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE6 MNW‐16‐D4‐12 2/12/2013 10:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE9 MNW‐16‐D4‐7 2/12/2013 10:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6PE8 MNW‐16‐D4‐2 2/12/2013 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CG0 MNW‐16‐D4‐17 8/20/2012 8:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CF9 MNW‐16‐D4‐12 8/20/2012 8:36 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CF8 MNW‐16‐D4‐7 8/20/2012 8:33 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UMNW‐16 (D4) D4 F6CF7 MNW‐16‐D4‐2 8/20/2012 8:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
Presbyterian unknown 5/10/2020 0:00 unknownPresbyterian unknown Presbyterian NA 1/13/2010 10:30 unknown GW µg/L 0.14 = 0.5 U 0.1 U 0.61 = 0.1 UPresbyterian unknown FGT00 NA 5/4/2000 0:00 OTHER GW µg/L 1 U 1 U 1 U 1 = 1 UPresbyterian unknown FGF62 NA 7/27/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UPresbyterian unknown FFZ71 NA 11/10/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 UPresbyterian unknown FFZ72 NA 11/10/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 U
Rutledge Linen unknown 5/10/2020 0:00 unknownRutledge Linen unknown notassigned‐11 NA 3/12/1987 0:00 unknown GW µg/L ND ND ND NDRutledge Linen unknown notassigned‐29 NA 1/22/1987 0:00 unknown GW µg/L T 1 =Rutledge Linen unknown notassigned‐10 NA 1/22/1987 0:00 unknown GW µg/L ND ND ND 1 =Rutledge Linen unknown notassigned‐28 NA 12/30/1986 0:00 unknown GW µg/L T 2 =Rutledge Linen unknown notassigned‐9 NA 12/30/1986 0:00 unknown GW µg/L ND ND ND 2 =
SFMW‐01 (S) NA 5/10/2020 0:00 unknownSFMW‐01 (S) S FQ885 NA 11/12/1997 0:00 unknown GW µg/L 1 = 1 U 1 = 0.7 J 1 USFMW‐01 (S) S FW894 NA 12/11/1996 0:00 unknown GW µg/L 1 = 1 U 2 = 0.8 J 1 USFMW‐01 (S) S FW893 NA 12/11/1996 0:00 unknown GW µg/L 1 = 1 U 1 = 0.9 J 1 USFMW‐01 (S) S FX009 NA 9/2/1993 0:00 unknown GW µg/L 3 = 1 U 4 = 2 = NDSFMW‐01 (S) S FQ927 NA 5/20/1993 0:00 unknown GW µg/L 6 J 10 U 2 J NDSFMW‐01 (S) S 2749 NA 6/1/1990 0:00 unknown GW µg/L 4 = 0.1 U 3.2 = 4.7 = NDSFMW‐01 (S) S OR‐90‐0815 NA 5/31/1990 0:00 unknown GW µg/L 3.4 = T 2.6 = 3.7 =
SFMW‐02 (S) NA 5/10/2020 0:00 unknownSFMW‐02 (S) S FX010 NA 8/31/1993 0:00 unknown GW µg/L 2 = 2 = 3 = 2 = NDSFMW‐02 (S) S FQ933 NA 5/20/1993 0:00 unknown GW µg/L 7 J 3 J 3 J NDSFMW‐02 (S) S 2766 NA 6/1/1990 0:00 unknown GW µg/L 7.1 = 0.25 = 9 = 6.6 = NDSFMW‐02 (S) S OR‐90‐0813 NA 5/31/1990 0:00 unknown GW µg/L 4.1 = T 4.5 = 4.4 =SFMW‐02 (S) S OR‐90‐0814 NA 5/31/1990 0:00 unknown GW µg/L 4.3 = T 4.6 = 4.4 =
SFMW‐03 (S) NA 5/10/2020 0:00 unknownSFMW‐03 (S) S FGF95 NA 8/2/1999 0:00 unknown GW µg/L 1 = 2 = 2 = 2 = 1 USFMW‐03 (S) S FQ882 NA 11/12/1997 0:00 unknown GW µg/L 2 = 3 = 1 = 2 = 1 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 36 OF 64
011524
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐03 (S) S FW895 NA 12/12/1996 0:00 unknown GW µg/L 1 = 3 = 1 = 2 = 1 USFMW‐03 (S) S FX011 NA 8/31/1993 0:00 unknown GW µg/L 3 = 1 = 3 = 3 = NDSFMW‐03 (S) S FQ926 NA 5/20/1993 0:00 unknown GW µg/L 7 J 10 U 3 J NDSFMW‐03 (S) S 2751 NA 6/1/1990 0:00 unknown GW µg/L 7.2 = 0.4 = 15.3 = 11.1 = NDSFMW‐03 (S) S OR‐90‐0812 NA 5/31/1990 0:00 unknown GW µg/L 4.7 = T 5.5 = 7.6 =
SFMW‐04 (S) NA 5/10/2020 0:00 unknownSFMW‐04 (S) S FX084 NA 5/2/2000 0:00 BAIL GW µg/L 1 = 1 U 1 = 1 = 1 USFMW‐04 (S) S FQ872 NA 11/6/1997 0:00 unknown GW µg/L 1 = 1 U 1 = 1 = 1 USFMW‐04 (S) S FX012 NA 8/31/1993 0:00 unknown GW µg/L 3 = 0.8 J 4 = 2 = NDSFMW‐04 (S) S FQ925 NA 5/20/1993 0:00 unknown GW µg/L ND 6 J 10 U 2 J NDSFMW‐04 (S) S 2752 NA 6/1/1990 0:00 unknown GW µg/L 7.8 = 0.1 U 8 = 6.2 = NDSFMW‐04 (S) S OR‐90‐0809 NA 5/31/1990 0:00 unknown GW µg/L 4.4 = T 5.9 = 4.2 =
SFMW‐05 (S) NA 5/10/2020 0:00 unknownSFMW‐05 (S) S FGF93 NA 8/2/1999 0:00 unknown GW µg/L 1 = 1 U 0.9 LJ 3 = 1 USFMW‐05 (S) S FQ811 NA 11/6/1997 0:00 unknown GW µg/L 2 = 1 U 1 = 3 = 1 USFMW‐05 (S) S FW879 NA 12/9/1996 0:00 unknown GW µg/L 2 = 1 U 2 = 4 = NDSFMW‐05 (S) S FX013 NA 8/31/1993 0:00 unknown GW µg/L 3 = 1 U 3 = 5 = NDSFMW‐05 (S) S FQ930 NA 5/20/1993 0:00 unknown GW µg/L 6 J 10 U 5 J NDSFMW‐05 (S) S FQ929 NA 5/20/1993 0:00 unknown GW µg/L 7 J 10 U 5 J ND
SFMW‐06 (I) NA 5/10/2020 0:00 unknownSFMW‐06 (I) I FGF92 NA 8/2/1999 0:00 unknown GW µg/L 6 = 1 U 4 = 24 = 1 USFMW‐06 (I) I FQ886 NA 11/12/1997 0:00 unknown GW µg/L 8 = 1 U 4 = 34 = 1 USFMW‐06 (I) I FW886 NA 12/11/1996 0:00 unknown GW µg/L 9 = 1 U 5 = 32 D NDSFMW‐06 (I) I FW887 NA 12/11/1996 0:00 unknown GW µg/L 8 = 1 U 4 = 33 D NDSFMW‐06 (I) I FX014 NA 8/31/1993 0:00 unknown GW µg/L 6 = 1 U 3 = 25 = NDSFMW‐06 (I) I FX019 NA 8/31/1993 0:00 unknown GW µg/L 6 = 1 U 3 = 26 E NDSFMW‐06 (I) I FQ932 NA 5/20/1993 0:00 unknown GW µg/L 9 J 10 U 20 = ND
SFMW‐07 (S) NA 5/10/2020 0:00 unknownSFMW‐07 (S) S FX083 NA 5/2/2000 0:00 BAIL GW µg/L 1 = 1 U 0.9 LJ 0.6 LJ 1 USFMW‐07 (S) S FGG02 NA 8/3/1999 0:00 unknown GW µg/L 1 = 1 U 1 = 0.6 LJ 1 USFMW‐07 (S) S FQ869 NA 11/6/1997 0:00 unknown GW µg/L 0.9 J 1 U 0.7 J 0.5 J 1 USFMW‐07 (S) S FW897 NA 12/12/1996 0:00 unknown GW µg/L 0.8 J 1 U 1 = 0.5 J 1 USFMW‐07 (S) S FX015 NA 8/31/1993 0:00 unknown GW µg/L 2 = 1 U 2 = 0.8 J NDSFMW‐07 (S) S FQ931 NA 5/20/1993 0:00 unknown GW µg/L 5 J 10 U 10 U ND
SFMW‐08 (S) NA 5/10/2020 0:00 unknownSFMW‐08 (S) S FQ864 NA 11/6/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐09 (I1) NA 5/10/2020 0:00 unknownSFMW‐09 (I1) I1 FW591 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 4 = 1 U 2 = 5 = 1 USFMW‐09 (I1) I1 FW561 NA 2/9/2000 0:00 unknown GW µg/L 3 = 1 U 2 = 4 = 1 USFMW‐09 (I1) I1 FGR63 NA 11/2/1999 0:00 unknown GW µg/L 5 = 1 U 5 = 3 = 1 USFMW‐09 (I1) I1 FGF41 NA 7/27/1999 0:00 unknown GW µg/L 3 = 1 U 2 = 4 = 1 USFMW‐09 (I1) I1 FQ868 NA 11/6/1997 0:00 unknown GW µg/L 0.8 J 1 U 1 U 1 = 1 USFMW‐09 (I1) I1 FQ867 NA 11/6/1997 0:00 unknown GW µg/L 0.8 J 1 U 1 U 0.8 J 1 U
SFMW‐10 (I2) 5/10/2020 0:00 unknownSFMW‐10 (I2) I2 SFMW‐10‐I2‐8‐022014 SFMW‐10‐I2‐8 2/17/2014 9:08 PDB GW µg/L 2.2 = 0.5 U 0.8 = 20.3 = 0.5 USFMW‐10 (I2) I2 F6PH7 SFMW‐10‐I2‐2 2/13/2013 0:00 PDB GW µg/L 3.2 = 0.5 U 1.7 = 16 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 37 OF 64
011525
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐10 (I2) I2 F6PH8 SFMW‐10‐I2‐5 2/13/2013 0:00 PDB GW µg/L 4.2 = 0.5 U 1.9 = 20 = 0.5 USFMW‐10 (I2) I2 F6PH9 SFMW‐10‐I2‐8 2/13/2013 0:00 PDB GW µg/L 4.3 = 0.5 U 1.9 = 21 = 0.5 USFMW‐10 (I2) I2 F6CA9 SFMW‐10‐I2‐5 8/20/2012 11:15 PDB GW µg/L 4.1 = 0.5 U 2.9 = 15 = 0.5 USFMW‐10 (I2) I2 F6CB0 SFMW‐10‐I2‐8 8/20/2012 10:59 PDB GW µg/L 4.7 = 0.5 U 3.3 = 18 = 0.5 USFMW‐10 (I2) I2 F6CA8 SFMW‐10‐I2‐2 8/20/2012 10:56 PDB GW µg/L 5.1 = 0.5 U 6.1 = 8.4 = 0.5 USFMW‐10 (I2) I2 F5G89 SFMW‐10‐I2‐8 2/27/2012 9:13 PDB GW µg/L 3.6 = 0.5 U 2.4 = 12 = 0.5 USFMW‐10 (I2) I2 F5G88 SFMW‐10‐I2‐5 2/27/2012 9:12 PDB GW µg/L 3 = 0.5 U 1.9 = 11 = 0.5 USFMW‐10 (I2) I2 F5G87 SFMW‐10‐I2‐2 2/27/2012 9:10 PDB GW µg/L 4 = 0.5 U 5 = 5.5 = 0.5 USFMW‐10 (I2) I2 F4ED6 SFMW‐10‐I2‐8‐Q311 8/22/2011 13:47 PDB GW µg/L 2.7 LJ 5.0 U 1.4 LJ 8.8 = 2.0 USFMW‐10 (I2) I2 F4ED5 SFMW‐10‐I2‐5‐Q311 8/22/2011 13:46 PDB GW µg/L 4.3 LJ 5.0 U 2.1 LJ 13 = 2.0 USFMW‐10 (I2) I2 F4ED4 SFMW‐10‐I2‐2‐Q311 8/22/2011 13:45 PDB GW µg/L 3.5 LJ 5.0 U 3.4 LJ 6.1 = 2.0 USFMW‐10 (I2) I2 SFMW‐10‐I2‐8‐Q111 SFMW‐10‐I2‐8 3/24/2011 10:50 PDB GW µg/L 2.4 = 0.5 U 1.1 = 6.2 = 0.5 USFMW‐10 (I2) I2 SFMW‐10‐I2‐5‐Q111 SFMW‐10‐I2‐5 3/24/2011 10:45 PDB GW µg/L 2.3 = 0.5 U 1.0 = 6.1 = 0.5 USFMW‐10 (I2) I2 SFMW‐10‐I2‐2‐Q111 SFMW‐10‐I2‐2 3/24/2011 10:40 PDB GW µg/L 1.9 = 0.5 U 0.9 = 3.3 = 0.5 USFMW‐10 (I2) I2 F3LW2 SFMW‐10‐I2‐Q310 8/30/2010 10:33 PDB GW µg/L 2.4 = 0.5 U 1.2 = 6.9 = 0.5 USFMW‐10 (I2) I2 FGF42 NA 7/27/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐10 (I2) I2 FQ865 NA 11/6/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐11 (S) 5/10/2020 0:00 unknownSFMW‐11 (S) S FQ888 NA 11/13/1997 0:00 unknown GW µg/L 0.8 J 1 U 1 = 1 U 1 U
SFMW‐12 (I1) 5/10/2020 0:00 unknownSFMW‐12 (I1) I1 F6PJ0 SFMW‐12‐I1‐2 2/13/2013 0:00 PDB GW µg/L 0.5 = 0.5 U 0.5 U 0.33 LJ 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐2‐Q111 SFMW‐12‐I1‐2 2/14/2011 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐12 (I1) I1 F3LW4 SFMW‐12‐I1‐5‐Q310 8/31/2010 11:40 PDB GW µg/L 0.46 LJ 0.5 U 0.5 U 0.51 = 0.5 USFMW‐12 (I1) I1 F3LW5 SFMW‐12‐I1‐8‐Q310 8/31/2010 11:40 PDB GW µg/L 0.52 = 0.5 U 0.5 U 0.58 = 0.5 USFMW‐12 (I1) I1 F3LW3 SFMW‐12‐I1‐2‐Q310 8/31/2010 11:40 PDB GW µg/L 0.54 = 0.5 U 0.21 LJ 0.61 = 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐8_100201 SFMW‐12‐I1‐8 2/1/2010 9:24 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 = 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐5_100201 SFMW‐12‐I1‐5 2/1/2010 9:23 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 = 0.5 USFMW‐12 (I1) I1 SFMW‐12‐I1‐2_100201 SFMW‐12‐I1‐2 2/1/2010 9:21 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 = 0.5 USFMW‐12 (I1) I1 F3B64 SFMW‐12‐I1‐8 10/26/2009 10:59 PDB GW µg/L 0.54 = 0.5 U 0.5 U 0.49 LJ 0.5 USFMW‐12 (I1) I1 F3B63 SFMW‐12‐I1‐5 10/26/2009 10:54 PDB GW µg/L 0.57 = 0.5 U 0.5 U 0.51 = 0.5 USFMW‐12 (I1) I1 F3B62 SFMW‐12‐I1‐2 10/26/2009 10:51 PDB GW µg/L 0.56 = 0.5 U 0.5 U 0.55 = 0.5 USFMW‐12 (I1) I1 FGF55 NA 7/27/1999 0:00 unknown GW µg/L 1 = 1 U 0.9 J 2 = 1 USFMW‐12 (I1) I1 FQ889 NA 11/13/1997 0:00 unknown GW µg/L 2 = 1 U 1 = 2 = 1 U
SFMW‐13 (I2) 5/10/2020 0:00 unknownSFMW‐13 (I2) I2 F6PJ1 SFMW‐13‐I2‐5 2/13/2013 0:00 PDB GW µg/L 1 = 0.5 U 0.25 LJ 1.2 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐5‐Q111 SFMW‐13‐I2‐5 2/14/2011 12:55 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐8‐Q310 SFMW13 I2‐8 9/23/2010 13:15 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.0 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐5‐Q310 SFMW13 I2‐5 9/23/2010 13:14 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I2‐2‐Q310 SFMW13 I2‐2 9/23/2010 13:13 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.0 = 0.5 USFMW‐13 (I2) I2 F3LW8 SFMW‐13‐I2‐Q310 8/31/2010 10:15 PDB GW µg/L 0.75 = 0.5 U 0.5 U 0.94 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I1‐8_100201 SFMW‐13‐I1‐8 2/1/2010 9:08 PDB GW µg/L 1 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I1‐5_100201 SFMW‐13‐I1‐5 2/1/2010 9:04 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.4 = 0.5 USFMW‐13 (I2) I2 SFMW‐13‐I1‐2_100201 SFMW‐13‐I1‐2 2/1/2010 9:01 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐13 (I2) I2 F3B67 SFMW‐13‐I2‐8 10/26/2009 10:42 PDB GW µg/L 1 = 0.5 U 0.37 LJ 1 = 0.5 USFMW‐13 (I2) I2 F3B66 SFMW‐13‐I2‐5 10/26/2009 10:39 PDB GW µg/L 0.85 = 0.5 U 0.32 LJ 0.87 = 0.5 USFMW‐13 (I2) I2 F3B65 SFMW‐13‐I2‐2 10/26/2009 10:36 PDB GW µg/L 0.74 = 0.5 U 0.5 U 0.72 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 38 OF 64
011526
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐13 (I2) I2 FX087 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 2 = 1 U 1 = 3 = 1 USFMW‐13 (I2) I2 FW557 NA 2/9/2000 0:00 unknown GW µg/L 2 = 1 U 0.9 LJ 2 = 1 USFMW‐13 (I2) I2 FGR58 NA 11/2/1999 0:00 unknown GW µg/L 3 = 1 U 3 = 2 = 1 USFMW‐13 (I2) I2 FGF56 NA 7/27/1999 0:00 unknown GW µg/L 2 = 1 U 1 = 4 = 1 USFMW‐13 (I2) I2 FQ891 NA 11/13/1997 0:00 unknown GW µg/L 3 = 1 U 2 = 7 = 1 U
SFMW‐14 (D1) 5/10/2020 0:00 unknownSFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐022014‐FD SFMW‐14‐D1‐2‐FD 2/17/2014 10:25 PDB GW µg/L 0.7 = 0.5 U 0.5 U 14.8 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐022014 SFMW‐14‐D1‐2 2/17/2014 9:25 PDB GW µg/L 0.8 = 0.5 U 0.5 U 14.8 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐0813 SFMW‐14‐D1‐2 8/13/2013 9:18 PDB WG µg/L 0.9 = 0.5 U 0.5 U 18.3 = 0.5 USFMW‐14 (D1) D1 F6PJ4 SFMW‐14‐D1‐5 2/18/2013 0:00 PDB GW µg/L 0.86 = 0.5 U 0.21 LJ 12 = 0.5 USFMW‐14 (D1) D1 F6PJ3 SFMW‐14‐D1‐8 2/18/2013 0:00 PDB GW µg/L 0.88 = 0.5 U 0.26 LJ 12 = 0.5 USFMW‐14 (D1) D1 F6PJ2 SFMW‐14‐D1‐2 2/18/2013 0:00 PDB GW µg/L 0.94 = 0.5 U 0.29 LJ 13 = 0.5 USFMW‐14 (D1) D1 F6CB3 SFMW‐14‐D1‐8 8/20/2012 12:35 PDB GW µg/L 0.75 = 0.062 LJ 0.19 LJ 14 = 0.5 USFMW‐14 (D1) D1 F6CB2 SFMW‐14‐D1‐5 8/20/2012 12:32 PDB GW µg/L 0.82 = 0.5 U 0.14 LJ 16 = 0.5 USFMW‐14 (D1) D1 F6CB1 SFMW‐14‐D1‐2 8/20/2012 12:28 PDB GW µg/L 0.84 = 0.5 U 0.24 LJ 17 = 0.5 USFMW‐14 (D1) D1 F5G46 SFMW‐14‐D1‐8 2/27/2012 10:39 PDB GW µg/L 0.58 = 0.5 U 0.5 U 7.5 = 0.5 USFMW‐14 (D1) D1 F5G45 SFMW‐14‐D1‐5 2/27/2012 10:36 PDB GW µg/L 0.65 = 0.5 U 0.5 U 8.7 = 0.5 USFMW‐14 (D1) D1 F5G44 SFMW‐14‐D1‐2 2/27/2012 10:34 PDB GW µg/L 0.58 = 0.5 U 0.5 U 7.3 = 0.5 USFMW‐14 (D1) D1 F4EE0 SFMW‐14‐D1‐8‐FD‐Q311 8/22/2011 14:33 PDB GW µg/L 5.0 U 5.0 U 5.0 U 7.9 = 2.0 USFMW‐14 (D1) D1 F4ED9 SFMW‐14‐D1‐8‐Q311 8/22/2011 14:32 PDB GW µg/L 5.0 U 5.0 U 5.0 U 8.5 = 2.0 USFMW‐14 (D1) D1 F4ED8 SFMW‐14‐D1‐5‐Q311 8/22/2011 14:31 PDB GW µg/L 5.0 U 5.0 U 5.0 U 6.9 = 2.0 USFMW‐14 (D1) D1 F4ED7 SFMW‐14‐D1‐2‐Q311 8/22/2011 14:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 7.4 = 2.0 USFMW‐14 (D1) D1 SFMW‐14‐D1‐2‐Q111 SFMW‐14‐D1‐2 2/14/2011 9:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4.6 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐5‐Q111 SFMW‐14‐D1‐5 2/14/2011 9:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4.3 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐D1‐8‐Q111 SFMW‐14‐D1‐8 2/14/2011 9:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4.5 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐I1‐Q310‐FD SFMW‐14‐I1‐Q310‐FD 9/9/2010 9:14 PDB GW µg/L 1.0 = 0.5 U 0.5 U 7.7 = 0.5 USFMW‐14 (D1) D1 SFMW‐14‐I1‐Q310 SFMW‐14‐I1‐Q310 9/9/2010 9:13 PDB GW µg/L 1.0 = 0.5 U 0.5 U 8.2 = 0.5 USFMW‐14 (D1) D1 FGF54 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐14 (D1) D1 FQ887 NA 11/13/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐15 (S) 5/10/2020 0:00 unknownSFMW‐15 (S) S F2RW1 SFMW‐15‐S‐12 4/14/2008 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐15 (S) S FGF84 NA 8/2/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐15 (S) S FEF64 NA 8/4/1998 0:00 unknown GW µg/L 0.3 J 1 U 1 U 1 U 1 USFMW‐15 (S) S 9711055‐1 NA 11/18/1997 0:00 unknown GW µg/L <1 <1 <1 <1 <5SFMW‐15 (S) S FQ899 NA 11/18/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐16 (I1) 5/10/2020 0:00 unknownSFMW‐16 (I1) I1 SFMW‐16‐I1‐8‐022014 SFMW‐16‐I1‐8 2/18/2014 9:33 PDB GW µg/L 0.8 = 0.5 U 0.5 U 5.8 = 0.5 USFMW‐16 (I1) I1 F6PJ5 SFMW‐16‐I1‐2 2/12/2013 0:00 PDB GW µg/L 0.96 = 0.5 U 0.17 LJ 6.5 = 0.5 USFMW‐16 (I1) I1 F6PJ6 SFMW‐16‐I1‐5 2/12/2013 0:00 PDB GW µg/L 0.95 = 0.5 U 0.18 LJ 7.1 = 0.5 USFMW‐16 (I1) I1 F6PJ7 SFMW‐16‐I1‐8 2/12/2013 0:00 PDB GW µg/L 1.5 = 0.5 U 0.31 LJ 8.3 = 0.5 USFMW‐16 (I1) I1 F6CB7 SFMW‐16‐I1‐8 8/20/2012 13:15 PDB GW µg/L 0.97 = 0.5 U 0.18 LJ 9.9 = 0.5 USFMW‐16 (I1) I1 F6CB6 SFMW‐16‐I1‐5 8/20/2012 13:10 PDB GW µg/L 0.86 = 0.5 U 0.16 LJ 9.6 = 0.5 USFMW‐16 (I1) I1 F6CB5 SFMW‐16‐I1‐2‐FD 8/20/2012 13:07 PDB GW µg/L 0.82 = 0.5 U 0.15 LJ 8.9 = 0.5 USFMW‐16 (I1) I1 F6CB4 SFMW‐16‐I1‐2 8/20/2012 13:06 PDB GW µg/L 0.85 = 0.5 U 0.16 LJ 9.1 = 0.5 USFMW‐16 (I1) I1 F5G91 SFMW‐16‐I1‐2‐FD 2/27/2012 11:37 PDB GW µg/L 0.92 = 0.5 U 0.2 LJ 7 = 0.5 USFMW‐16 (I1) I1 F5G93 SFMW‐16‐I1‐8 2/27/2012 10:45 PDB GW µg/L 0.97 = 0.5 U 0.23 LJ 7.6 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 39 OF 64
011527
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐16 (I1) I1 F5G92 SFMW‐16‐I1‐5 2/27/2012 10:40 PDB GW µg/L 0.85 = 0.5 U 0.19 LJ 6.7 = 0.5 USFMW‐16 (I1) I1 F5G90 SFMW‐16‐I1‐2 2/27/2012 10:37 PDB GW µg/L 0.87 = 0.5 U 0.2 LJ 6.5 = 0.5 USFMW‐16 (I1) I1 F4EE1 SFMW‐16‐I1‐2‐Q311 8/22/2011 8:50 PDB GW µg/L 1.4 LJ 5.0 U 5.0 U 12 = 2.0 USFMW‐16 (I1) I1 F4EE2 SFMW‐16‐I1‐5‐Q311 8/22/2011 8:50 PDB GW µg/L 1.3 LJ 5.0 U 5.0 U 13 = 2.0 USFMW‐16 (I1) I1 F4EE3 SFMW‐16‐I1‐8‐Q311 8/22/2011 8:50 PDB GW µg/L 1.3 LJ 5.0 U 5.0 U 5.0 U 2.0 USFMW‐16 (I1) I1 SFMW‐16‐I1‐8‐Q111‐FD SFMW‐16‐I1‐8 2/14/2011 11:51 PDB GW µg/L 2.9 = 0.5 U 0.9 = 20.3 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐8‐Q111 SFMW‐16‐I1‐8 2/14/2011 10:51 PDB GW µg/L 3 = 0.5 U 0.9 = 20.8 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐5‐Q111 SFMW‐16‐I1‐5 2/14/2011 10:49 PDB GW µg/L 0.9 = 0.5 U 0.5 U 7.1 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐2‐Q111 SFMW‐16‐I1‐2 2/14/2011 10:47 PDB GW µg/L 0.8 = 0.5 U 0.5 U 6.2 = 0.5 USFMW‐16 (I1) I1 F3LR5 SFMW‐16‐I1‐Q310 9/2/2010 9:20 PDB GW µg/L 3.9 = 0.5 U 1.4 = 32 = 0.5 USFMW‐16 (I1) I2 SFMW‐16‐I2‐8_100201 SFMW‐16‐I1‐8 2/1/2010 13:25 PDB GW µg/L 1.1 = 0.5 U 0.5 U 7.4 = 0.5 USFMW‐16 (I1) I2 SFMW‐16‐I2‐5_100201 SFMW‐16‐I1‐5 2/1/2010 13:22 PDB GW µg/L 1 = 0.5 U 0.5 U 6.3 = 0.5 USFMW‐16 (I1) I1 SFMW‐16‐I1‐2_100201 SFMW‐16‐I1‐2 2/1/2010 13:20 PDB GW µg/L 1.2 = 0.5 U 0.5 U 7.6 = 0.5 USFMW‐16 (I1) I1 F2RW3 SFMW‐16‐I1‐5 4/14/2008 0:00 PDB GW µg/L 0.74 = 0.5 U 0.5 U 3.4 = 0.5 USFMW‐16 (I1) I1 F2RW2 SFMW‐16‐I1‐2 4/14/2008 0:00 PDB GW µg/L 0.82 = 0.5 U 0.19 LJ 4.8 = 0.5 USFMW‐16 (I1) I1 F2RW4 SFMW‐16‐I1‐8 4/14/2008 0:00 PDB GW µg/L 0.95 = 0.5 U 0.5 U 5.6 = 0.5 USFMW‐16 (I1) I1 FGF69 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 = 1 USFMW‐16 (I1) I1 FEF75 NA 8/4/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 0.2 J 1 USFMW‐16 (I1) I1 FQ900 NA 11/18/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐17 (I2) 5/10/2020 0:00 unknownSFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐022014‐FD SFMW‐17‐I2‐8 2/18/2014 10:23 PDB GW µg/L 3.9 = 0.5 U 2.2 = 7.6 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐022014 SFMW‐17‐I2‐8‐FD 2/18/2014 9:23 PDB GW µg/L 3.1 = 0.5 U 1.8 = 3.7 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐0813 SFMW‐17‐I2‐8 8/12/2013 12:37 PDB WG µg/L 5.1 = 0.5 U 2.6 = 23.6 = 0.5 USFMW‐17 (I2) I2 F6PJ9 SFMW‐17‐I2‐8‐FD 2/12/2013 0:00 PDB GW µg/L 5.5 = 0.5 U 2.4 = 20 = 0.5 USFMW‐17 (I2) I2 F6PJ8 SFMW‐17‐I2‐8 2/12/2013 0:00 PDB GW µg/L 6 = 0.5 U 3.1 = 20 = 0.5 USFMW‐17 (I2) I2 F6CB8 SFMW‐17‐I2‐8 8/20/2012 13:43 PDB GW µg/L 7.4 = 0.5 U 6.6 = 16 = 0.5 USFMW‐17 (I2) I2 F5G94 SFMW‐17‐I2‐8 2/27/2012 10:55 PDB GW µg/L 6.1 = 0.5 U 8.7 = 5.7 = 0.5 USFMW‐17 (I2) I2 F4EE5 SFMW‐17‐I2‐8‐FD‐Q311 8/22/2011 9:05 PDB GW µg/L 8.9 = 5.0 U 14 = 13 = 2.0 USFMW‐17 (I2) I2 F4EE4 SFMW‐17‐I2‐8‐Q311 8/22/2011 9:00 PDB GW µg/L 6.9 = 5.0 U 10 = 7.0 = 2.0 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q111 SFMW‐17‐I2‐8 2/14/2011 10:45 PDB GW µg/L 12.8 = 0.5 U 17.5 = 7.3 J 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q310 SFMW‐17‐I2‐8‐Q310 9/7/2010 11:35 PDB GW µg/L 2.5 = 0.5 U 1.5 = 3.4 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8_100201 SFMW‐17‐I2‐8 2/1/2010 13:40 PDB GW µg/L 6 = 0.5 U 5.7 = 9.4 = 0.5 USFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q209 SFMW‐17‐I2‐8 4/21/2009 8:23 PDB GW µg/L 6.6 J 0.5 UJ 10.9 J 6.1 J 0.5 JSFMW‐17 (I2) I2 F2RW7 SFMW‐17‐I2‐8 4/14/2008 0:00 PDB GW µg/L 3.5 = 0.5 U 1.7 = 20 = 0.5 USFMW‐17 (I2) I2 F2RW5 SFMW‐17‐I2‐2 4/14/2008 0:00 PDB GW µg/L 0.81 = 0.5 U 0.1 LJ 3.2 = 0.5 UJSFMW‐17 (I2) I2 F2RW6 SFMW‐17‐I2‐5 4/14/2008 0:00 PDB GW µg/L 1.1 = 0.5 U 0.5 U 3.5 = 0.5 UJSFMW‐17 (I2) I2 SFMW‐17‐I2‐8‐Q407 SFMW‐17‐I2‐8 10/1/2007 8:07 PDB GW µg/L 2.8 = 0.5 U 0.8 = 17.6 = 0.5 USFMW‐17 (I2) I2 F1NS0 SFMW‐17‐I2‐8 7/13/2005 8:06 PDB GW µg/L 0.94 = 0.5 U 0.27 LJ 7.4 = 0.5 USFMW‐17 (I2) I2 F1NR9 SFMW‐17‐I2‐5 7/13/2005 8:04 PDB GW µg/L 0.53 = 0.5 U 0.11 LJ 2.8 = 0.28 LJSFMW‐17 (I2) I2 F1NR8 SFMW‐17‐I2‐2 7/13/2005 8:00 PDB GW µg/L 0.52 = 0.5 U 0.1 LJ 2.6 = 0.3 LJSFMW‐17 (I2) I2 F1DM3 SFMW‐17‐I2‐8 4/19/2005 8:40 PDB GW µg/L 0.83 = 0.5 U 0.27 LJ 7.6 = 0.5 USFMW‐17 (I2) I2 F1DM2 SFMW‐17‐I2‐5 4/19/2005 8:38 PDB GW µg/L 0.61 = 0.5 U 0.12 LJ 3.3 = 0.34 LJSFMW‐17 (I2) I2 F1DM1 SFMW‐17‐I2‐2 4/19/2005 8:36 PDB GW µg/L 0.57 = 0.5 U 0.1 LJ 3.1 = 0.5 USFMW‐17 (I2) I2 F17K9 SFMW‐17‐I2‐8 11/9/2004 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 4 = 0.5 USFMW‐17 (I2) I2 F17K8 SFMW‐17‐I2‐5 11/9/2004 9:23 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.3 = 0.5 USFMW‐17 (I2) I2 F17K7 SFMW‐17‐I2‐2 11/9/2004 9:14 PDB GW µg/L 0.5 U 0.5 U 0.5 U 2 = 0.43 LJ
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 40 OF 64
011528
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐17 (I2) I2 SFMW17‐020221 NA 2/21/2002 13:55 unknown GW µg/L 1 U 1 U 1 U 5.1 = 1 USFMW‐17 (I2) I2 FGF70 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐17 (I2) I2 FEF79 NA 8/5/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐17 (I2) I2 FQ898 NA 11/18/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐18 (I1) NA 5/10/2020 0:00 unknownSFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐022014 SFMW‐18‐I1‐8 2/17/2014 11:05 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.8 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐0813FD SFMW‐18‐I1‐8FD 8/12/2013 10:40 PDB WG µg/L 0.7 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐0813 SFMW‐18‐I1‐8 8/12/2013 9:40 PDB WG µg/L 0.8 = 0.5 U 0.5 U 1.4 = 0.5 USFMW‐18 (I1) I1 F6PK0 SFMW‐18‐I1‐8 2/13/2013 0:00 PDB GW µg/L 0.98 = 0.5 U 0.29 LJ 1.7 = 0.5 USFMW‐18 (I1) I1 F6CD1 SFMW‐18‐I1‐8 8/21/2012 9:55 PDB GW µg/L 0.85 = 0.5 U 0.28 LJ 1.4 = 0.5 USFMW‐18 (I1) I1 F5G95 SFMW‐18‐I1‐8 2/27/2012 10:00 PDB GW µg/L 0.86 = 0.5 U 0.31 LJ 1.3 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐Q111 SFMW‐18‐I1‐8 2/14/2011 11:00 PDB GW µg/L 1 = 0.5 U 0.5 U 2.2 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5‐Q111 SFMW‐18‐I1‐5 2/14/2011 10:55 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.6 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2‐Q111‐FD SFMW‐18‐I1‐2 2/14/2011 10:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2‐Q111 SFMW‐18‐I1‐2 2/14/2011 10:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8‐Q310 SFMW‐18‐I1‐8‐Q310 9/7/2010 12:05 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.6 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5‐Q310‐FD SFMW‐18‐I1‐5‐Q310‐FD 9/7/2010 12:00 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.6 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5‐Q310 SFMW‐18‐I1‐5‐Q310 9/7/2010 11:55 PDB GW µg/L 0.9 = 0.5 U 0.5 U 1.5 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2‐Q310 SFMW‐18‐I1‐2‐Q310 9/7/2010 11:50 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐8_100201 SFMW‐18‐I1‐8 2/1/2010 11:11 PDB GW µg/L 1.2 = 0.5 U 0.5 U 2 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐5_100201 SFMW‐18‐I1‐5 2/1/2010 11:09 PDB GW µg/L 1 = 0.5 U 0.5 U 1.9 = 0.5 USFMW‐18 (I1) I1 SFMW‐18‐I1‐2_100201 SFMW‐18‐I1‐2 2/1/2010 11:07 PDB GW µg/L 0.8 = 0.5 U 0.5 U 1.4 = 0.5 USFMW‐18 (I1) I1 F3B72 SFMW‐18‐I1‐8 10/26/2009 12:18 PDB GW µg/L 1.1 = 0.5 U 0.44 LJ 1.8 J 0.5 USFMW‐18 (I1) I1 F3B71 SFMW‐18‐I1‐5 10/26/2009 12:13 PDB GW µg/L 0.9 = 0.5 U 0.35 LJ 1.6 = 0.5 USFMW‐18 (I1) I1 F3B69 SFMW‐18‐I1‐2 10/26/2009 12:10 PDB GW µg/L 0.82 = 0.5 U 0.36 LJ 1.3 = 0.5 USFMW‐18 (I1) I1 FW595 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 4 = 1 U 1 = 17 = 1 USFMW‐18 (I1) I1 FW594 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 5 = 1 U 1 = 18 = 1 USFMW‐18 (I1) I1 FGG03 NA 8/3/1999 0:00 unknown GW µg/L 4 = 1 U 2 = 15 = 1 USFMW‐18 (I1) I1 FQ873 NA 11/6/1997 0:00 unknown GW µg/L 4 = 1 U 1 = 18 = 1 U
SFMW‐19 (I2) NA 5/10/2020 0:00 unknownSFMW‐19 (I2) I2 FGG53 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 LJ 10 U 10 U 66 = 10 USFMW‐19 (I2) I2 FFZ90 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 LJ 10 U 10 U 72 = 10 USFMW‐19 (I2) I2 FW569 NA 2/10/2000 0:00 unknown GW µg/L 9 = 1 U 1 = 86 = 1 USFMW‐19 (I2) I2 FW570 NA 2/10/2000 0:00 unknown GW µg/L 9 = 1 U 1 = 90 = 1 USFMW‐19 (I2) I2 FGR76 NA 11/3/1999 0:00 unknown GW µg/L 13 = 1 U 4 = 73 = 1 USFMW‐19 (I2) I2 FGR74 NA 11/3/1999 0:00 unknown GW µg/L 14 = 1 U 4 = 76 = 1 USFMW‐19 (I2) I2 FGG06 NA 8/3/1999 0:00 unknown GW µg/L 10 = 1 U 2 = 75 = 1 USFMW‐19 (I2) I2 FQ870 NA 11/6/1997 0:00 unknown GW µg/L 7 = 1 U 0.9 J 36 = 1 USFMW‐19 (I2) I2 FQ851 NA 11/4/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐20 (I1) 5/10/2020 0:00 unknownSFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐022014 SFMW‐20‐I1‐5 2/17/2014 8:57 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐0813 SFMW‐20‐I1‐5 8/13/2013 10:50 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐20 (I1) I1 F6PK1 SFMW‐20‐I1‐5 2/19/2013 0:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.16 LJ 0.5 USFMW‐20 (I1) I1 F6CG1 SFMW‐20‐I1‐5 8/20/2012 14:49 PDB GW µg/L 0.5 U 0.037 LJ 0.5 U 0.11 LJ 0.5 USFMW‐20 (I1) I1 F5G96 SFMW‐20‐I1‐5 2/28/2012 12:02 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 USFMW‐20 (I1) I1 F4EE6 SFMW‐20‐I1‐5‐Q311 8/22/2011 14:25 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 41 OF 64
011529
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐20 (I1) I1 F3S39 SFMW‐20‐I1‐5 2/15/2011 11:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5_100201 SFMW‐20‐I1‐5 2/1/2010 15:02 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐20 (I1) I1 F3B04 SFMW‐20‐I1‐5 10/26/2009 12:10 PDB GW µg/L 0.43 LJ 0.5 U 0.5 U 0.75 = 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐Q209 SFMW‐20‐I1‐5 4/21/2009 9:20 PDB GW µg/L 0.8 J 0.5 UJ 0.5 UJ 1.1 J 0.5 UJSFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐Q408 SFMW‐20‐I1‐5 10/7/2008 10:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐20 (I1) I1 F2RW8 SFMW‐20‐I1‐5 4/14/2008 0:00 PDB GW µg/L 1.1 = 0.5 U 0.49 LJ 2.3 = 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1‐5‐Q407 SFMW‐20‐I1‐5 10/2/2007 10:19 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐20 (I1) I1 SFMW‐20‐I1_070219 SFMW‐20‐I1‐5 2/19/2007 11:53 PDB GW µg/L 1.2 JL 0.5 UJ 0.7 JL 2.6 JL 0.5 UJSFMW‐20 (I1) I1 F2691 SFMW‐20‐I1‐5 8/28/2006 9:55 PDB GW µg/L 0.52 = 0.5 U 0.5 U 1 = 0.5 USFMW‐20 (I1) I1 F1YP2 SFMW‐20‐I1‐5 2/6/2006 13:11 PDB GW µg/L 1.2 = 0.5 U 0.64 = 2.3 = 0.5 USFMW‐20 (I1) I1 F1NT4 SFMW‐20‐I1‐8 7/11/2005 11:58 PDB GW µg/L 0.92 = 0.5 U 0.68 = 3.4 = 0.5 USFMW‐20 (I1) I1 F1NT3 SFMW‐20‐I1‐5 7/11/2005 11:55 PDB GW µg/L 0.92 = 0.5 U 0.69 = 3.4 = 0.5 USFMW‐20 (I1) I1 F1NT2 SFMW‐20‐I1‐2 7/11/2005 11:53 PDB GW µg/L 0.81 = 0.5 U 0.46 LJ 2.2 = 0.5 USFMW‐20 (I1) I1 F1DN7 SFMW‐20‐I1‐8 4/18/2005 14:40 PDB GW µg/L 2.7 = 0.15 LJ 1.4 = 5.2 = 0.17 LJSFMW‐20 (I1) I1 F1DN6 SFMW‐20‐I1‐5 4/18/2005 14:38 PDB GW µg/L 2 = 0.11 LJ 1 = 4.3 = 0.18 LJSFMW‐20 (I1) I1 F1DN5 SFMW‐20‐I1‐2 4/18/2005 14:36 PDB GW µg/L 2.3 = 0.13 LJ 1.1 = 4.8 = 0.17 LJSFMW‐20 (I1) I1 F17W4 SFMW‐20‐I1‐8 11/8/2004 15:20 PDB GW µg/L 1.6 = 0.5 U 0.77 = 3.2 = 0.5 USFMW‐20 (I1) I1 F17W3 SFMW‐20‐I1‐5 11/8/2004 15:15 PDB GW µg/L 1.3 = 0.5 U 0.69 = 2.9 = 0.5 USFMW‐20 (I1) I1 F17W2 SFMW‐20‐I1‐2 11/8/2004 15:10 PDB GW µg/L 1.3 = 0.5 U 0.64 = 2.9 = 0.5 USFMW‐20 (I1) I1 SFMW20‐020305 NA 3/5/2002 13:35 unknown GW µg/L 1.2 = 1 U 1 U 2.3 = 1 USFMW‐20 (I1) I1 FGF81 NA 8/2/1999 0:00 unknown GW µg/L 2 = 1 U 0.9 LJ 4 = 1 USFMW‐20 (I1) I1 FQ849 NA 11/4/1997 0:00 unknown GW µg/L 2 = 1 U 0.8 J 4 = 1 U
SFMW‐21 (I2) NA 5/10/2020 0:00 unknownSFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐022014 SFMW‐21‐I2‐12 2/17/2014 9:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐022014 SFMW‐21‐I2‐17 2/17/2014 9:27 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐0813 SFMW‐21‐I2‐17 8/13/2013 10:35 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.6 =SFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐0813 SFMW‐21‐I2‐12 8/13/2013 10:30 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F6PK3 SFMW‐21‐I2‐17 2/19/2013 9:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F6PK2 SFMW‐21‐I2‐12 2/19/2013 9:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F6CG4 SFMW‐21‐I2‐17‐FD 8/20/2012 14:44 PDB GW µg/L 0.12 LJ 0.5 U 0.5 U 0.097 LJ 0.5 USFMW‐21 (I2) I2 F6CG3 SFMW‐21‐I2‐17 8/20/2012 14:43 PDB GW µg/L 0.12 LJ 0.5 U 0.5 U 0.080 LJ 0.5 USFMW‐21 (I2) I2 F6CG2 SFMW‐21‐I2‐12 8/20/2012 14:39 PDB GW µg/L 0.12 LJ 0.031 LJ 0.054 LJ 0.10 LJ 0.5 USFMW‐21 (I2) I2 F5G99 SFMW‐21‐12‐17‐FD 2/28/2012 12:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F5G98 SFMW‐21‐I2‐17 2/28/2012 11:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F5G97 SFMW‐21‐I2‐12 2/28/2012 11:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F4EE8 SFMW‐21‐I2‐17‐Q311 8/22/2011 14:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐21 (I2) I2 F4EE7 SFMW‐21‐I2‐12‐Q311 8/22/2011 14:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐21 (I2) I2 F3S41 SFMW‐21‐I2‐17 2/15/2011 11:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐21 (I2) I2 F3S40 SFMW‐21‐I2‐12 2/15/2011 11:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐12_100201 SFMW‐21‐I2‐12 2/1/2010 14:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17_100201 SFMW‐21‐I2‐17 2/1/2010 14:28 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.5 U 0.5 USFMW‐21 (I2) I2 F3B05 SFMW‐21‐I2‐12 10/26/2009 11:51 PDB GW µg/L 0.38 LJ 0.5 U 0.5 U 0.37 LJ 0.5 USFMW‐21 (I2) I2 F3B06 SFMW‐21‐I2‐17 10/26/2009 11:48 PDB GW µg/L 0.78 = 0.5 U 0.34 LJ 0.73 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐Q209 SFMW‐21‐I2‐17 4/21/2009 9:13 PDB GW µg/L 0.9 J 0.5 UJ 0.5 UJ 0.9 J 0.5 UJSFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐Q209 SFMW‐21‐I2‐12 4/21/2009 9:11 PDB GW µg/L 0.6 J 0.5 UJ 0.5 UJ 0.6 J 0.5 UJSFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐Q408 SFMW‐21‐I2‐17 10/7/2008 9:59 PDB GW µg/L 1.2 = 0.5 U 0.5 U 0.9 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 42 OF 64
011530
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐Q408 SFMW‐21‐I2‐12 10/7/2008 9:57 PDB GW µg/L 0.9 = 0.5 U 0.5 U 0.8 = 0.5 USFMW‐21 (I2) I2 F2RW9 SFMW‐21‐I2‐12 4/14/2008 0:00 PDB GW µg/L 1.2 = 0.5 U 0.49 LJ 1.1 = 0.5 USFMW‐21 (I2) I2 F2RX0 SFMW‐21‐I2‐17 4/14/2008 0:00 PDB GW µg/L 1.4 = 0.5 U 0.58 = 1.2 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17‐Q407 SFMW‐21‐I2‐17 10/1/2007 13:35 PDB GW µg/L 1.7 = 0.5 U 0.8 = 1.6 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐12‐Q407 SFMW‐21‐I2‐12 10/1/2007 13:32 PDB GW µg/L 1.6 = 0.5 U 0.8 = 1.6 = 0.5 USFMW‐21 (I2) I2 SFMW‐21‐I2‐17_070219 SFMW‐21‐I2‐17 2/19/2007 11:42 PDB GW µg/L 1.9 JL 0.5 UJ 1 JL 2.2 JL 0.5 UJSFMW‐21 (I2) I2 SFMW‐21‐I2‐12_070219 SFMW‐21‐I2‐12 2/19/2007 11:38 PDB GW µg/L 1.6 JL 0.5 UJ 0.8 JL 1.8 JL 0.5 UJSFMW‐21 (I2) I2 F2693 SFMW‐21‐I2‐17 8/28/2006 10:15 PDB GW µg/L 1.5 = 0.5 U 0.73 = 1.5 = 0.5 USFMW‐21 (I2) I2 F2692 SFMW‐21‐I2‐12 8/28/2006 10:12 PDB GW µg/L 1.6 = 0.5 U 0.79 = 1.7 = 0.5 USFMW‐21 (I2) I2 F1YP5 SFMW‐21‐I2‐17 2/6/2006 13:05 PDB GW µg/L 2.9 = 0.5 U 1.5 = 3.1 = 0.5 USFMW‐21 (I2) I2 F1YP4 SFMW‐21‐I2‐12 2/6/2006 13:04 PDB GW µg/L 2.6 = 0.5 U 1.3 = 2.8 = 0.5 USFMW‐21 (I2) I2 F1YP3 SFMW‐21‐I2‐7 2/6/2006 13:02 PDB GW µg/L 0.8 = 0.5 U 1.4 = 0.5 U 0.5 USFMW‐21 (I2) I2 F1NT9 SFMW‐21‐I2‐17 7/11/2005 12:20 PDB GW µg/L 2.9 = 0.5 U 2.3 = 4.7 = 0.5 USFMW‐21 (I2) I2 F1NT8 SFMW‐21‐I2‐12 7/11/2005 12:18 PDB GW µg/L 2.4 = 0.5 U 3.3 = 0.99 = 0.76 =SFMW‐21 (I2) I2 F1NT7 SFMW‐21‐I2‐7 7/11/2005 12:15 PDB GW µg/L 2.9 = 0.5 U 2.3 = 4.6 = 0.5 USFMW‐21 (I2) I2 F1NT5 SFMW‐21‐I2‐2 7/11/2005 12:10 PDB GW µg/L 1.3 = 0.5 U 2.5 = 0.41 LJ 0.5 USFMW‐21 (I2) I2 F1DP2 SFMW‐21‐I2‐17 4/18/2005 14:56 PDB GW µg/L 3.6 = 0.5 U 1.8 = 4.3 = 0.26 LJSFMW‐21 (I2) I2 F1DP1 SFMW‐21‐I2‐12 4/18/2005 14:54 PDB GW µg/L 5 = 0.1 LJ 2.8 = 5.9 = 0.5 USFMW‐21 (I2) I2 F1DP0 SFMW‐21‐I2‐7 4/18/2005 14:52 PDB GW µg/L 4 = 0.5 U 3.8 = 0.94 = 0.5 USFMW‐21 (I2) I2 F1DN8 SFMW‐21‐I2‐2 4/18/2005 14:48 PDB GW µg/L 3.6 = 0.5 U 4 = 0.77 = 0.5 USFMW‐21 (I2) I2 F17C5 SFMW‐21‐I2 11/9/2004 9:05 LFS GW µg/L 3.3 = 0.5 U 1.9 = 4.5 J^ 0.51 =SFMW‐21 (I2) I2 F17W9 SFMW‐21‐I2‐17 11/8/2004 15:55 PDB GW µg/L 4 = 0.5 U 2.4 = 5.1 = 0.41 LJSFMW‐21 (I2) I2 F17W8 SFMW‐21‐I2‐12 11/8/2004 15:50 PDB GW µg/L 4.2 = 0.5 U 2.3 = 5.2 = 0.5 USFMW‐21 (I2) I2 F17W7 SFMW‐21‐I2‐7 11/8/2004 15:45 PDB GW µg/L 4 = 0.5 U 3.2 = 0.5 U 1.4 =SFMW‐21 (I2) I2 F17W5 SFMW‐21‐I2‐2 11/8/2004 15:40 PDB GW µg/L 3.9 = 0.5 U 4 = 0.5 U 1.7 =SFMW‐21 (I2) I2 SFMW21‐020227 NA 2/27/2002 15:31 unknown GW µg/L 3.7 = 1 U 2.2 = 5.5 = 1 USFMW‐21 (I2) I2 FGS94 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 5 = 1 U 3 = 6 = 1 USFMW‐21 (I2) I2 FW558 NA 2/9/2000 0:00 unknown GW µg/L 5 = 1 U 3 = 6 = 1 USFMW‐21 (I2) I2 FGR67 NA 11/2/1999 0:00 unknown GW µg/L 10 = 1 U 10 = 6 = 1 USFMW‐21 (I2) I2 FGF83 NA 8/2/1999 0:00 unknown GW µg/L 8 = 0.6 LJ 4 = 10 = 1 USFMW‐21 (I2) I2 FQ853 NA 11/4/1997 0:00 unknown GW µg/L 6 = 0.6 J 3 = 9 = 1 U
SFMW‐22 (D1) NA 5/10/2020 0:00 unknownSFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐022014 SFMW‐22‐D1‐8 2/17/2014 9:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐022014‐FD SFMW‐22‐D1‐8 2/17/2014 9:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐0813 SFMW‐22‐D1‐8 8/13/2013 11:00 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 = 0.5 USFMW‐22 (D1) D1 F6PK4 SFMW‐22‐D1‐8 2/19/2013 9:30 PDB GW µg/L 0.21 LJ 0.5 U 0.21 LJ 0.35 LJ 0.5 USFMW‐22 (D1) D1 F6CD0 SFMW‐22‐D1‐8 8/21/2012 10:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 F5GA0 SFMW‐22‐D1‐8 2/28/2012 12:30 PDB GW µg/L 0.34 LJ 0.5 U 0.5 U 0.69 = 0.5 USFMW‐22 (D1) D1 F4EE9 SFMW‐22‐D1‐8‐Q311 8/22/2011 14:05 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.4 LJ 2.0 USFMW‐22 (D1) D1 F3S42 SMFW‐22‐D1‐8 2/15/2011 12:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐22 (D1) D1 F3RM5 SFMW‐22‐D1‐8 12/14/2010 10:22 PDB GW µg/L 0.4 LJ 0.5 U 0.14 LJ 0.84 = 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8_100202 SFMW‐22‐D1‐8 2/2/2010 7:52 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐22 (D1) D1 F3B07 SMFW‐22‐D1‐8 10/26/2009 12:42 PDB GW µg/L 0.37 LJ 0.5 U 0.5 U 0.66 = 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐Q209 SMFW‐22‐D1‐8 4/21/2009 9:37 PDB GW µg/L 0.6 J 0.5 UJ 0.5 UJ 1.0 J 0.5 UJSFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐Q408 SMFW‐22‐D1‐8 10/7/2008 10:27 PDB GW µg/L 0.7 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐22 (D1) D1 SFMW‐22‐D1‐8‐Q407 SFMW‐22‐D1‐8 10/2/2007 10:38 PDB GW µg/L 1.6 = 0.5 U 0.5 = 3.4 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 43 OF 64
011531
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐22 (D1) D1 F2694 SFMW‐22‐D1‐8 8/28/2006 10:25 PDB GW µg/L 1.7 = 0.5 U 0.61 = 3.5 = 0.5 USFMW‐22 (D1) D1 F1NW2 SFMW‐22‐D1‐8 7/11/2005 11:10 PDB GW µg/L 2.3 = 0.5 U 1.5 = 5.4 = 0.5 USFMW‐22 (D1) D1 F1NW1 SFMW‐22‐D1‐5 7/11/2005 11:05 PDB GW µg/L 2 = 0.5 U 1.3 = 4.3 = 0.5 USFMW‐22 (D1) D1 F1NW0 SFMW‐22‐D1‐2 7/11/2005 11:00 PDB GW µg/L 2.4 = 0.5 U 1.6 = 5.1 = 0.5 USFMW‐22 (D1) D1 F1DP5 SFMW‐22‐D1‐8 4/19/2005 12:50 PDB GW µg/L 3 = 0.5 U 1.2 = 5.1 = 0.18 LJSFMW‐22 (D1) D1 F1DP4 SFMW‐22‐D1‐5 4/19/2005 12:48 PDB GW µg/L 2.9 = 0.5 U 1.3 = 4.1 = 0.5 USFMW‐22 (D1) D1 F1DP3 SFMW‐22‐D1‐2 4/19/2005 12:46 PDB GW µg/L 2.9 = 0.5 U 1.3 = 3.9 = 0.18 LJSFMW‐22 (D1) D1 F17X2 SFMW‐22‐D1‐8 11/8/2004 14:00 PDB GW µg/L 3.3 = 0.5 U 1.2 = 5.3 = 0.5 USFMW‐22 (D1) D1 F17X1 SFMW‐22‐D1‐5 11/8/2004 13:55 PDB GW µg/L 3.4 = 0.5 U 1.5 = 5 = 0.5 USFMW‐22 (D1) D1 F17X0 SFMW‐22‐D1‐2 11/8/2004 13:50 PDB GW µg/L 2.7 = 0.5 U 1.4 = 3.7 = 0.5 USFMW‐22 (D1) D1 SFMW22‐020305 NA 3/5/2002 15:55 unknown GW µg/L 5.1 = 1 U 2.8 = 8.5 = 1 USFMW‐22 (D1) D1 FW593 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 7 = 1 U 3 = 9 = 1 USFMW‐22 (D1) D1 FGF90 NA 8/2/1999 0:00 unknown GW µg/L 7 = 1 U 4 = 11 = 1 USFMW‐22 (D1) D1 FQ848 NA 11/4/1997 0:00 unknown GW µg/L 7 = 1 U 4 = 11 = 1 U
SFMW‐23 (D2) NA 5/10/2020 0:00 unknownSFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐022014 SFMW‐23‐D2‐5 2/17/2014 9:03 PDB GW µg/L 1.6 = 0.5 U 0.5 U 4 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐0813 SFMW‐23‐D2‐5 8/13/2013 11:05 PDB WG µg/L 0.5 U 0.5 U 0.5 U 3.7 = 0.5 USFMW‐23 (D2) D2 F6PK5 SFMW‐23‐D2‐5 2/19/2013 9:20 PDB GW µg/L 0.72 = 0.5 U 0.16 LJ 1.7 = 0.5 USFMW‐23 (D2) D2 F6CG6 SFMW‐23‐D2‐5 8/20/2012 14:58 PDB GW µg/L 0.099 LJ 0.19 LJ 0.5 U 0.39 LJ 0.5 USFMW‐23 (D2) D2 F5GA1 SFMW‐23‐D2‐5 2/28/2012 12:13 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.39 LJ 0.5 USFMW‐23 (D2) D2 F4EF0 SFMW‐23‐D2‐5‐Q311 8/22/2011 14:15 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐23 (D2) D2 F3S43 SFMW‐23‐D2‐5 2/15/2011 11:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5_100201 SFMW‐23‐D2‐5 2/1/2010 14:47 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 USFMW‐23 (D2) D2 F3B08 SFMW‐23‐D2‐5 10/26/2009 12:26 PDB GW µg/L 0.28 LJ 0.5 U 0.5 U 0.74 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐FD‐Q209 SFMW‐23‐D2‐5‐FD 4/21/2009 9:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.0 J 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐Q209 SFMW‐23‐D2‐5 4/21/2009 9:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.0 J 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐Q408 SFMW‐23‐D2‐5 10/7/2008 10:22 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 USFMW‐23 (D2) D2 F2RX1 SFMW‐23‐D2‐5 4/14/2008 0:00 PDB GW µg/L 0.33 LJ 0.44 LJ 0.5 U 1.5 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2‐5‐Q407 SFMW‐23‐D2‐5 10/2/2007 10:26 PDB GW µg/L 0.5 U 0.5 = 0.5 U 1.8 = 0.5 USFMW‐23 (D2) D2 SFMW‐23‐D2_070219 SFMW‐23‐D2‐5 2/19/2007 12:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.8 JL 0.5 UJSFMW‐23 (D2) D2 F2695 SFMW‐23‐D2‐5 8/28/2006 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.1 = 0.5 USFMW‐23 (D2) D2 F1YP6 SFMW‐23‐D2‐5 2/6/2006 13:17 PDB GW µg/L 0.93 = 0.5 U 0.5 U 3.8 = 0.5 USFMW‐23 (D2) D2 F1NW5 SFMW‐23‐D2‐8 7/11/2005 11:35 PDB GW µg/L 4.5 = 0.5 U 1.9 = 11 = 0.12 LJSFMW‐23 (D2) D2 F1NW4 SFMW‐23‐D2‐5 7/11/2005 11:33 PDB GW µg/L 5.7 = 0.5 U 2.1 = 18 = 0.16 LJSFMW‐23 (D2) D2 F1NW3 SFMW‐23‐D2‐2 7/11/2005 11:30 PDB GW µg/L 4.1 = 0.5 U 1.9 = 9.1 J 0.11 LJSFMW‐23 (D2) D2 F1D94 SFMW‐23‐D2 4/21/2005 8:05 LFS GW µg/L 5.8 = 0.5 U 5.2 = 6.2 = 0.5 USFMW‐23 (D2) D2 F1DP8 SFMW‐23‐D2‐8 4/19/2005 13:12 PDB GW µg/L 5.3 = 0.5 U 2.5 = 13 = 0.18 LJSFMW‐23 (D2) D2 F1DP7 SFMW‐23‐D2‐5 4/19/2005 13:10 PDB GW µg/L 5.3 = 0.5 U 2.2 = 14 = 0.15 LJSFMW‐23 (D2) D2 F1DP6 SFMW‐23‐D2‐2 4/19/2005 13:08 PDB GW µg/L 4.8 = 0.5 U 2 = 11 = 0.16 LJSFMW‐23 (D2) D2 F17C7 SFMW‐23‐D2 11/8/2004 15:24 LFS GW µg/L 6 = 0.5 U 2.2 = 16 J 0.27 LJSFMW‐23 (D2) D2 F17X5 SFMW‐23‐D2‐8 11/8/2004 14:35 PDB GW µg/L 6.3 = 0.5 U 2.6 = 20 = 0.5 USFMW‐23 (D2) D2 F17X4 SFMW‐23‐D2‐5 11/8/2004 14:30 PDB GW µg/L 6.6 = 0.5 U 2.6 = 22 = 0.5 USFMW‐23 (D2) D2 F17X3 SFMW‐23‐D2‐2 11/8/2004 14:25 PDB GW µg/L 8.1 = 0.5 U 2.5 = 19 J 0.34 LJSFMW‐23 (D2) D2 SFMW23‐020307 NA 3/7/2002 11:00 unknown GW µg/L 6.8 = 1 U 2.9 = 27 = 1 USFMW‐23 (D2) D2 SFMW73‐020307 NA 3/7/2002 11:00 unknown GW µg/L 7.1 = 1 U 3.4 = 27 = 1 USFMW‐23 (D2) D2 FGT02 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 10 = 2 U 3 = 32 = 2 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 44 OF 64
011532
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐23 (D2) D2 FW568 NA 2/10/2000 0:00 unknown GW µg/L 10 = 1 U 4 = 38 = 1 USFMW‐23 (D2) D2 FGR65 NA 11/3/1999 0:00 unknown GW µg/L 16 = 1 U 12 = 35 = 1 USFMW‐23 (D2) D2 FGR66 NA 11/3/1999 0:00 unknown GW µg/L 16 = 1 U 12 = 39 = 1 USFMW‐23 (D2) D2 FGF87 NA 8/2/1999 0:00 unknown GW µg/L 9 = 1 U 4 = 42 = 1 USFMW‐23 (D2) D2 FGF88 NA 8/2/1999 0:00 unknown GW µg/L 12 = 1 U 5 = 42 = 1 USFMW‐23 (D2) D2 FQ852 NA 11/4/1997 0:00 unknown GW µg/L 9 = 1 U 3 = 35 = 1 U
SFMW‐24 (S) NA 5/10/2020 0:00 unknownSFMW‐24 (S) S 200001473 NA 7/10/2000 0:00 unknown GW µg/L 1.1 = <0.5 U 0.7 = 1.2 = <0.5 USFMW‐24 (S) S 200001474 NA 7/10/2000 0:00 unknown GW µg/L 1.1 = <0.5 U 0.7 = 1.2 = <0.5 USFMW‐24 (S) S FW582 NA 5/1/2000 0:00 BAIL GW µg/L 10 = 5 U 3 LJ 35 = 5 USFMW‐24 (S) S FGF67 NA 7/29/1999 0:00 unknown GW µg/L 2 = 1 U 0.9 LJ 2 = 1 USFMW‐24 (S) S FQ860 NA 11/5/1997 0:00 unknown GW µg/L 2 = 1 U 1 = 2 = 1 U
SFMW‐25 (I1) NA 5/10/2020 0:00 unknownSFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐022014 SFMW‐25‐I1‐5 2/18/2014 10:18 PDB GW µg/L 2.3 = 0.5 U 0.9 = 4.6 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐0813FD SFMW‐25‐I1‐5FD 8/12/2013 9:26 PDB WG µg/L 3.3 = 0.5 U 0.7 = 8 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐0813 SFMW‐25‐I1‐5 8/12/2013 8:26 PDB WG µg/L 3.2 = 0.5 U 0.7 = 7.7 = 0.5 USFMW‐25 (I1) I1 F6PN3 SFMW‐25‐I1‐5 2/12/2013 13:10 PDB GW µg/L 3.9 = 0.5 U 0.76 = 8.9 = 0.5 USFMW‐25 (I1) I1 F6CC1 SFMW‐25‐I1‐5‐FD 8/21/2012 8:36 PDB GW µg/L 3.4 = 0.5 U 0.62 = 8.5 = 0.5 USFMW‐25 (I1) I1 F6CC0 SFMW‐25‐I1‐5 8/21/2012 8:21 PDB GW µg/L 3.6 = 0.034 LJ 0.65 = 8.7 = 0.5 USFMW‐25 (I1) I1 F5GA3 SFMW‐25‐I1‐5‐FD 2/28/2012 9:00 PDB GW µg/L 3 = 0.5 U 0.57 = 8.2 = 0.5 USFMW‐25 (I1) I1 F5GA2 SFMW‐25‐I1‐5 2/28/2012 9:00 PDB GW µg/L 3 = 0.5 U 0.58 = 9.4 = 0.5 USFMW‐25 (I1) I1 F4EF1 SFMW‐25‐I1‐5‐Q311 8/22/2011 11:05 PDB GW µg/L 5.2 = 5.0 U 5.0 U 14 = 2.0 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q111 SFMW‐25‐I1‐5 2/14/2011 10:00 PDB GW µg/L 3.6 = 0.5 U 0.6 = 11 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q310 SFMW‐25‐I1‐5‐Q310 9/7/2010 8:50 PDB GW µg/L 3.9 = 0.5 U 0.7 = 9.9 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5_100201 SFMW‐25‐I1‐5 2/1/2010 14:45 PDB GW µg/L 4 = 0.5 U 0.8 = 9.6 J 0.5 USFMW‐25 (I1) I1 F3B74 SFMW‐25‐I1‐5 10/26/2009 13:45 PDB GW µg/L 3.7 = 0.5 U 0.79 = 10 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q209 SFMW‐25‐I1‐5 4/20/2009 10:20 PDB GW µg/L 4.6 J 0.5 U 1.1 J 11.8 J 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q408 SFMW‐25‐I1‐5 10/6/2008 12:57 PDB GW µg/L 5.3 = 0.5 U 1.6 = 10.4 = 0.5 USFMW‐25 (I1) I1 F2RX2 SFMW‐25‐I1‐5 4/14/2008 0:00 PDB GW µg/L 6.1 = 0.5 U 2.3 = 13 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1‐5‐Q407 SFMW‐25‐I1‐5 10/1/2007 12:20 PDB GW µg/L 5.2 = 0.5 U 1.7 = 11.6 = 0.5 USFMW‐25 (I1) I1 SFMW‐25‐I1_070219 SFMW‐25‐I1‐5 2/19/2007 8:50 PDB GW µg/L 6 JL 0.5 UJ 1.9 JL 15.4 JL 0.5 UJSFMW‐25 (I1) I1 F2696 SFMW‐25‐I1‐5 8/28/2006 11:10 PDB GW µg/L 3.7 = 0.5 U 1 = 10 = 0.5 USFMW‐25 (I1) I1 F1YQ6 SFMW‐25‐I1‐5 2/6/2006 13:51 PDB GW µg/L 6.3 = 0.5 U 1.6 = 17 = 0.5 UJSFMW‐25 (I1) I1 F1NS8 SFMW‐25‐I1‐8 7/12/2005 14:12 PDB GW µg/L 7.3 = 0.5 U 1.8 = 20 J 0.5 USFMW‐25 (I1) I1 F1NS7 SFMW‐25‐I1‐5‐FD 7/12/2005 14:09 PDB GW µg/L 7.4 = 0.5 U 1.8 = 21 = 0.5 USFMW‐25 (I1) I1 F1NS6 SFMW‐25‐I1‐5 7/12/2005 14:08 PDB GW µg/L 0.27 R 0.5 UR 0.5 UR 0.43 R 0.5 URSFMW‐25 (I1) I1 F1NS5 SFMW‐25‐I1‐2 7/12/2005 14:07 PDB GW µg/L 7 = 0.5 U 2 = 20 = 0.5 USFMW‐25 (I1) I1 F1DN1 SFMW‐25‐I1‐8 4/18/2005 11:35 PDB GW µg/L 8.8 J 0.5 U 2.5 J 25 J 0.5 USFMW‐25 (I1) I1 F1DM9 SFMW‐25‐I1‐5 4/18/2005 11:31 PDB GW µg/L 7.7 = 0.5 U 2.3 = 23 = 0.14 LJSFMW‐25 (I1) I1 F1DM8 SFMW‐25‐I1‐2 4/18/2005 11:29 PDB GW µg/L 7.4 = 0.5 U 2.3 = 23 = 0.11 LJSFMW‐25 (I1) I1 F17L4 SFMW‐25‐I1‐8 11/9/2004 14:06 PDB GW µg/L 6.1 = 0.5 U 1.5 = 17 = 0.5 USFMW‐25 (I1) I1 F17L2 SFMW‐25‐I1‐5 11/9/2004 14:02 PDB GW µg/L 6.5 = 0.5 U 1.6 = 18 = 0.5 USFMW‐25 (I1) I1 F17L1 SFMW‐25‐I1‐2 11/9/2004 14:00 PDB GW µg/L 4.9 = 0.5 U 1.2 = 10 = 0.5 USFMW‐25 (I1) I1 SFMW75‐020306 NA 3/6/2002 17:10 unknown GW µg/L 7.9 = 1 U 2.1 = 30 = 1 USFMW‐25 (I1) I1 SFMW25‐020306 NA 3/6/2002 17:10 unknown GW µg/L 8.5 = 1 U 2.1 = 30 = 1 USFMW‐25 (I1) I1 FX092 NA 5/3/2000 0:00 BAIL GW µg/L 10 = 5 U 5 U 34 = 5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 45 OF 64
011533
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐25 (I1) I1 FW576 NA 2/1/2000 0:00 unknown GW µg/L 13 = 1 U 3 = 15 = 1 USFMW‐25 (I1) I1 FGR82 NA 11/4/1999 0:00 unknown GW µg/L 17 = 1 U 8 = 47 = 1 USFMW‐25 (I1) I1 FGF74 NA 7/29/1999 0:00 unknown GW µg/L 13 = 1 U 4 = 42 = 1 USFMW‐25 (I1) I1 FGF73 NA 7/29/1999 0:00 unknown GW µg/L 12 = 1 U 4 = 44 = 1 USFMW‐25 (I1) I1 FQ862 NA 11/5/1997 0:00 unknown GW µg/L 13 = 1 U 4 = 54 = 1 U
SFMW‐26 (I2) NA 5/10/2020 0:00 unknownSFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐022014 SFMW‐26‐I2‐8 2/18/2014 10:30 PDB GW µg/L 1.2 = 0.5 U 0.5 U 2.2 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐022014 SFMW‐26‐I2‐2 2/18/2014 10:25 PDB GW µg/L 0.8 = 0.5 U 0.5 U 0.6 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐0813 SFMW‐26‐I2‐8 8/12/2013 8:53 PDB WG µg/L 1.3 = 0.5 U 0.5 U 2.9 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐0813 SFMW‐26‐I2‐2 8/12/2013 8:51 PDB WG µg/L 1.4 = 0.5 U 0.5 U 2.8 = 0.5 USFMW‐26 (I2) I2 F6PK8 SFMW‐26‐I2‐8 2/13/2013 13:10 PDB GW µg/L 1.5 = 0.13 LJ 0.12 LJ 3.1 = 0.5 USFMW‐26 (I2) I2 F6PK7 SFMW‐26‐I2‐2 2/13/2013 13:00 PDB GW µg/L 1.6 = 0.16 LJ 0.5 U 3.1 = 0.5 USFMW‐26 (I2) I2 F6CC3 SFMW‐26‐I2‐8 8/21/2012 8:32 PDB GW µg/L 0.29 LJ 22 J 0.062 LJ 110 J 0.5 USFMW‐26 (I2) I2 F6CC2 SFMW‐26‐I2‐2 8/21/2012 8:29 PDB GW µg/L 1.6 = 0.17 LJ 0.11 LJ 3.0 = 0.5 USFMW‐26 (I2) I2 F5GA5 SFMW‐26‐I2‐8 2/28/2012 9:15 PDB GW µg/L 1.4 = 0.15 LJ 0.11 LJ 3.7 = 0.5 USFMW‐26 (I2) I2 F5GA4 SFMW‐26‐I2‐2 2/28/2012 9:10 PDB GW µg/L 1.4 = 0.5 U 0.1 LJ 3.1 = 0.5 USFMW‐26 (I2) I2 F4EF3 SFMW‐26‐I2‐8‐Q311 8/22/2011 11:15 PDB GW µg/L 2.5 LJ 5.0 U 5.0 U 5.2 = 2.0 USFMW‐26 (I2) I2 F4EF2 SFMW‐26‐I2‐2‐Q311 8/22/2011 11:10 PDB GW µg/L 2.5 LJ 5.0 U 5.0 U 4.6 LJ 2.0 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q111 SFMW‐26‐I2‐8 2/14/2011 10:15 PDB GW µg/L 1.8 = 0.5 U 0.5 U 4.5 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I1‐2‐Q111 SFMW‐26‐I2‐2 2/14/2011 10:10 PDB GW µg/L 1.7 = 0.5 U 0.5 U 3.8 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q310 SFMW‐26‐I2‐8‐Q310 9/7/2010 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q310 SFMW‐26‐I2‐2‐Q310 9/7/2010 9:55 PDB GW µg/L 2.2 = 0.5 U 0.5 U 4.1 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2_100201 SFMW‐26‐I2‐2 2/1/2010 15:00 PDB GW µg/L 2.6 = 0.5 U 1 = 4 = 0.5 USFMW‐26 (I2) I2 F3B76 SFMW‐26‐I2‐8 10/26/2009 13:31 PDB GW µg/L 2.6 = 0.29 LJ 0.5 U 6.4 = 0.5 USFMW‐26 (I2) I2 F3B75 SFMW‐26‐I2‐2 10/26/2009 13:28 PDB GW µg/L 2.3 = 0.48 LJ 0.5 U 4.7 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q209 SFMW‐26‐I2‐8 4/20/2009 10:10 PDB GW µg/L 3.1 J 0.5 U 0.5 U 7.4 J 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q209 SFMW‐26‐I2‐2 4/20/2009 10:09 PDB GW µg/L 3.2 J 0.5 J 0.5 U 6.0 J 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q408 SFMW‐26‐I2‐2 10/6/2008 11:33 PDB GW µg/L 2.3 = 0.5 U 0.6 = 5 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q408 SFMW‐26‐I2‐8 10/6/2008 10:31 PDB GW µg/L 3.7 = 0.5 U 0.5 U 7.8 = 0.5 USFMW‐26 (I2) I2 F2RX3 SFMW‐26‐I2‐2 4/14/2008 0:00 PDB GW µg/L 4 = 0.5 U 1.5 = 5.5 = 0.5 USFMW‐26 (I2) I2 F2RX5 SFMW‐26‐I2‐8 4/14/2008 0:00 PDB GW µg/L 4.4 = 0.52 = 0.33 LJ 8.4 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8‐Q407 SFMW‐26‐I2‐8 10/1/2007 12:30 PDB GW µg/L 4.3 = 0.6 = 0.5 U 9.3 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐2‐Q407 SFMW‐26‐I2‐2 10/1/2007 12:28 PDB GW µg/L 4.4 = 0.8 = 0.5 U 8.2 = 0.5 USFMW‐26 (I2) I2 SFMW‐26‐I2‐8_070219 SFMW‐26‐I2‐8 2/19/2007 8:38 PDB GW µg/L 5.4 JL 0.5 JL 1.4 JL 9.7 JL 0.5 UJSFMW‐26 (I2) I2 SFMW‐26‐I2‐2_070219 SFMW‐26‐I2‐2 2/19/2007 8:30 PDB GW µg/L 5.5 JL 0.7 JL 0.9 JL 10.2 JL 0.5 UJSFMW‐26 (I2) I2 F2699 SFMW‐26‐I2‐8 8/28/2006 11:03 PDB GW µg/L 4.1 = 0.61 = 0.5 U 9.1 = 0.5 USFMW‐26 (I2) I2 F2697 SFMW‐26‐I2‐2 8/28/2006 10:59 PDB GW µg/L 4.8 = 0.93 = 0.57 = 9.3 = 0.5 USFMW‐26 (I2) I2 F1YQ9 SFMW‐26‐I2‐8 2/6/2006 13:56 PDB GW µg/L 6.2 = 0.95 = 0.7 = 13 = 0.5 USFMW‐26 (I2) I2 F1YQ7 SFMW‐26‐I2‐2 2/6/2006 13:48 PDB GW µg/L 6.4 = 1.3 = 0.52 = 12 = 0.5 USFMW‐26 (I2) I2 F1NT1 SFMW‐26‐I2‐8 7/12/2005 13:55 PDB GW µg/L 8.2 = 1.2 = 0.76 = 18 = 0.19 LJSFMW‐26 (I2) I2 F1NT0 SFMW‐26‐I2‐5 7/12/2005 13:53 PDB GW µg/L 7.3 = 1.1 = 0.55 = 13 J 0.14 LJSFMW‐26 (I2) I2 F1NS9 SFMW‐26‐I2‐2 7/12/2005 13:50 PDB GW µg/L 8.8 = 1.5 = 0.92 = 17 = 0.18 LJSFMW‐26 (I2) I2 F1DN4 SFMW‐26‐I2‐8 4/18/2005 11:56 PDB GW µg/L 9.7 = 0.79 = 1.8 = 20 = 0.19 LJSFMW‐26 (I2) I2 F1DN3 SFMW‐26‐I2‐5 4/18/2005 11:54 PDB GW µg/L 7.7 = 0.84 = 0.94 = 15 J 0.14 LJSFMW‐26 (I2) I2 F1DN2 SFMW‐26‐I2‐2 4/18/2005 11:50 PDB GW µg/L 10 = 1.2 = 1 = 20 = 0.17 LJSFMW‐26 (I2) I2 F17L7 SFMW‐26‐I2‐8 11/9/2004 14:20 PDB GW µg/L 8.1 = 0.55 = 0.72 = 19 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 46 OF 64
011534
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐26 (I2) I2 F17L6 SFMW‐26‐I2‐5 11/9/2004 14:17 PDB GW µg/L 9.2 = 0.9 = 0.64 = 20 J 0.35 LJSFMW‐26 (I2) I2 F17L5 SFMW‐26‐I2‐2 11/9/2004 14:15 PDB GW µg/L 8.8 = 0.65 = 0.48 LJ 16 = 0.5 USFMW‐26 (I2) I2 SFMW26‐020307 NA 3/7/2002 8:30 unknown GW µg/L 8.8 = 1 U 1.4 = 22 = 1 USFMW‐26 (I2) I2 FGG54 NA 5/5/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 = 1 U 1 = 23 = 1 USFMW‐26 (I2) I2 FGF75 NA 7/29/1999 0:00 unknown GW µg/L 7 = 1 U 2 = 23 = 1 USFMW‐26 (I2) I2 FQ861 NA 11/5/1997 0:00 unknown GW µg/L 7 = 1 U 2 = 22 = 1 U
SFMW‐27 (I2) NA 5/10/2020 0:00 unknownSFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐022014 SFMW‐27‐I2‐8 2/17/2014 11:17 PDB GW µg/L 4.9 = 0.5 U 2.5 = 13.4 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐0813 SFMW‐27‐I2‐8 8/12/2013 9:50 PDB WG µg/L 5.4 = 0.5 U 4.4 = 11.3 = 0.5 USFMW‐27 (I2) I2 F6PK9 SFMW‐27‐I2‐2 2/13/2013 0:00 PDB GW µg/L 5.9 = 0.5 U 6.5 = 4.5 = 0.5 USFMW‐27 (I2) I2 F6PL0 SFMW‐27‐I2‐5 2/13/2013 0:00 PDB GW µg/L 5.9 = 0.5 U 4.9 = 9 = 0.5 USFMW‐27 (I2) I2 F6PL1 SFMW‐27‐I2‐8 2/13/2013 0:00 PDB GW µg/L 6.3 = 0.5 U 5.6 = 9.8 = 0.5 USFMW‐27 (I2) I2 F6CC6 SFMW‐27‐I2‐8 8/21/2012 7:36 PDB GW µg/L 4.9 = 0.031 LJ 3.4 = 9.9 = 0.5 USFMW‐27 (I2) I2 F6CC5 SFMW‐27‐I2‐5 8/21/2012 7:33 PDB GW µg/L 4.9 = 0.041 LJ 2.9 = 9.4 = 0.5 USFMW‐27 (I2) I2 F6CC4 SFMW‐27‐I2‐2 8/21/2012 7:30 PDB GW µg/L 1.4 = 0.5 U 0.10 LJ 3.0 J 0.5 USFMW‐27 (I2) I2 F5GA8 SFMW‐27‐I2‐8 2/28/2012 8:55 PDB GW µg/L 4.6 = 0.5 U 3.9 = 9.1 = 0.5 USFMW‐27 (I2) I2 F5GA7 SFMW‐27‐I2‐5 2/28/2012 8:54 PDB GW µg/L 4.4 = 0.5 U 3.5 = 9.4 = 0.5 USFMW‐27 (I2) I2 F5GA6 SFMW‐27‐I2‐2 2/28/2012 8:53 PDB GW µg/L 5.3 = 0.5 U 4.7 = 9.5 = 0.5 USFMW‐27 (I2) I2 F4EF6 SFMW‐27‐I2‐8‐Q311 8/23/2011 8:13 PDB GW µg/L 6.7 = 5.0 U 4.7 LJ 13 = 2.0 USFMW‐27 (I2) I2 F4EF5 SFMW‐27‐I2‐5‐Q311 8/23/2011 8:10 PDB GW µg/L 9.3 = 5.0 U 6.6 = 17 = 2.0 USFMW‐27 (I2) I2 F4EF4 SFMW‐27‐I2‐2‐Q311 8/23/2011 8:07 PDB GW µg/L 7.9 = 5.0 U 5.8 = 13 = 2.0 USFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐Q111 SFMW‐27‐I2‐8 2/14/2011 13:52 PDB GW µg/L 6.4 = 0.5 U 5.3 = 8.4 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐5‐Q111 SFMW‐27‐I2‐5 2/14/2011 13:50 PDB GW µg/L 7.1 = 0.5 U 4.8 = 7.2 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐2‐Q111 SFMW‐27‐I2‐2 2/14/2011 13:48 PDB GW µg/L 6.9 = 0.5 U 4.7 = 6.6 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐8‐Q310 SFMW‐27‐I2‐8‐Q310 9/9/2010 9:54 PDB GW µg/L 4.4 = 0.5 U 0.5 U 13.7 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐5‐Q310 SFMW‐27‐I2‐5‐Q310 9/9/2010 9:52 PDB GW µg/L 3.9 = 0.5 U 0.5 U 8.0 = 0.5 USFMW‐27 (I2) I2 SFMW‐27‐I2‐2‐Q310 SFMW‐27‐I2‐2‐Q310 9/9/2010 9:50 PDB GW µg/L 3.2 = 0.5 U 0.5 U 5.7 = 0.5 USFMW‐27 (I2) I2 FGS84 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 9 = 1 U 1 = 22 = 1 USFMW‐27 (I2) I2 FW565 NA 2/10/2000 0:00 unknown GW µg/L 9 = 1 U 1 = 23 = 1 USFMW‐27 (I2) I2 FGR79 NA 11/4/1999 0:00 unknown GW µg/L 11 = 1 U 3 = 20 = 1 USFMW‐27 (I2) I2 FGG04 NA 8/3/1999 0:00 unknown GW µg/L 10 = 1 U 2 = 32 = 1 USFMW‐27 (I2) I2 FGG05 NA 8/3/1999 0:00 unknown GW µg/L 10 = 1 U 2 = 33 = 1 USFMW‐27 (I2) I2 FEF66 NA 7/30/1998 0:00 unknown GW µg/L 9 = 1 U 2 = 46 = 1 U
SFMW‐28 (I2) NA 5/10/2020 0:00 unknownSFMW‐28 (I2) I2 SFMW‐28‐I2‐8‐022014 SFMW‐28‐I2‐8 2/18/2014 11:12 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐022014 SFMW‐28‐I2‐5 2/18/2014 11:08 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐2‐022014 SFMW‐28‐I2‐2 2/18/2014 11:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐8‐0813 SFMW‐28‐I2‐8 8/12/2013 12:17 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐0813 SFMW‐28‐I2‐5 8/12/2013 12:14 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐2‐0813 SFMW‐28‐I2‐2 8/12/2013 12:12 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6PL4 SFMW‐28‐I2‐8 2/13/2013 10:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6PL3 SFMW‐28‐I2‐5 2/13/2013 10:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6PL2 SFMW‐28‐I2‐2 2/13/2013 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6CC9 SFMW‐28‐I2‐8 8/21/2012 9:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6CC8 SFMW‐28‐I2‐5 8/21/2012 9:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F6CC7 SFMW‐28‐I2‐2 8/21/2012 9:01 PDB GW µg/L 5.1 = 0.5 U 3.1 = 10 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 47 OF 64
011535
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐28 (I2) I2 F4EG0 SFMW‐28‐I2‐8‐FD‐Q311 8/22/2011 10:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 F4EF9 SFMW‐28‐I2‐8‐Q311 8/22/2011 10:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 F4EF8 SFMW‐28‐I2‐5‐Q311 8/22/2011 10:25 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 F4EF7 SFMW‐28‐I2‐2‐Q311 8/22/2011 10:20 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐Q111 SFMW‐28‐I2‐5 2/14/2011 14:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐8‐Q310 SFMW‐28‐I2‐8‐Q310 9/7/2010 12:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐5‐Q310 SFMW‐28‐I2‐5‐Q310 9/7/2010 12:41 PDB GW µg/L 2.3 = 0.5 U 0.5 U 5.2 = 0.5 USFMW‐28 (I2) I2 SFMW‐28‐I2‐2‐Q310 SFMW‐28‐I2‐2‐Q310 9/7/2010 12:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F3B33 SFMW‐28‐I2‐2 10/27/2009 9:11 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F3B35 SFMW‐28‐I2‐8 10/26/2009 10:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 F3B34 SFMW‐28‐I2‐5 10/26/2009 10:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐28 (I2) I2 FW592 NA 5/3/2000 0:00 GRN‐PUMP DUKE GW µg/L 7 = 1 = 1 U 10 = 1 USFMW‐28 (I2) I2 FW566 NA 2/10/2000 0:00 unknown GW µg/L 6 = 1 = 1 U 9 = 1 USFMW‐28 (I2) I2 FGR73 NA 11/3/1999 0:00 unknown GW µg/L 11 = 1 = 0.9 LJ 11 = 1 USFMW‐28 (I2) I2 FGF48 NA 7/28/1999 0:00 unknown GW µg/L 10 = 2 = 1 U 16 = 1 USFMW‐28 (I2) I2 FEF67 NA 7/30/1998 0:00 unknown GW µg/L 13 = 2 = 1 U 21 = 1 U
SFMW‐29 (I2) 5/10/2020 0:00 unknownSFMW‐29 (I2) I1 SFMW‐29‐I1‐5‐Q209 SFMW‐29‐I1‐5 4/21/2009 7:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I1 SFMW‐29‐I1‐5‐Q407 SFMW‐29‐I1‐5 10/1/2007 10:34 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1NS4 SFMW‐29‐I2‐8 7/13/2005 8:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1NS2 SFMW‐29‐I2‐2 7/13/2005 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1NS3 SFMW‐29‐I2‐5 7/13/2005 8:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1DM7 SFMW‐29‐I2‐8 4/18/2005 13:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1DM6 SFMW‐29‐I2‐5 4/18/2005 13:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F1DM5 SFMW‐29‐I2‐2 4/18/2005 13:39 PDB GW µg/L 0.5 UJv 0.5 U 0.5 UJv 0.5 U 0.5 USFMW‐29 (I2) I2 F17M0 SFMW‐29‐I2‐8 11/9/2004 11:39 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 F17L9 SFMW‐29‐I2‐5 11/9/2004 11:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.33 LJ 0.5 USFMW‐29 (I2) I2 F17L8 SFMW‐29‐I2‐2 11/9/2004 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐29 (I2) I2 SFMW29‐020221 NA 2/21/2002 16:13 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FX094 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FW564 NA 2/10/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FGR62 NA 11/2/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FGF49 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐29 (I2) I2 FEF68 NA 7/30/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐30 (I2) NA 5/10/2020 0:00 unknownSFMW‐30 (I2) I2 FGF50 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐30 (I2) I2 FEF72 NA 7/28/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐31 (I2) 5/10/2020 0:00 unknownSFMW‐31 (I2) I2 F6PL7 SFMW‐31‐I2‐8 2/19/2013 10:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 USFMW‐31 (I2) I2 F6PL6 SFMW‐31‐I2‐5 2/19/2013 10:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 USFMW‐31 (I2) I2 F6PL5 SFMW‐31‐I2‐2 2/19/2013 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.14 LJ 0.5 USFMW‐31 (I2) I2 F3S29 SFMW‐31‐I2‐8 2/15/2011 14:20 PDB GW µg/L 0.25 LJ 0.5 U 0.5 U 0.76 J 0.5 USFMW‐31 (I2) I2 F3S28 SFMW‐31‐I2‐5 2/15/2011 14:17 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐31 (I2) I2 F3S27 SFMW‐31‐I2‐2 2/15/2011 14:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 UJ 0.5 USFMW‐31 (I2) I2 F3LQ0 SFMW‐31‐I2‐8‐Q310 9/2/2010 13:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.44 LJ 0.5 USFMW‐31 (I2) I2 F3LP9 SFMW‐31‐I2‐5‐Q310 9/2/2010 13:35 PDB GW µg/L 0.21 LJ 0.5 U 0.5 U 0.47 LJ 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 48 OF 64
011536
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐31 (I2) I2 F3LP8 SFMW‐31‐I2‐2‐Q310 9/2/2010 13:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.44 LJ 0.5 USFMW‐31 (I2) I2 F3B12 SFMW‐31‐I2‐8 10/26/2009 14:01 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐31 (I2) I2 F3B11 SFMW‐31‐I2‐5 10/26/2009 13:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐31 (I2) I2 F3B10 SFMW‐31‐I2‐2 10/26/2009 13:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐31 (I2) I2 FX093 NA 5/3/2000 0:00 GRN‐PUMP NMED GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐31 (I2) I2 FGF51 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐31 (I2) I2 FX079 NA 7/27/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐32 (I2) NA 5/10/2020 0:00 unknownSFMW‐32 (I2) I2 F6PL8 SFMW‐32‐I2‐5 2/18/2013 10:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q111 SFMW‐32‐I2‐5 2/14/2011 12:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q209 SFMW‐32‐I2‐5 4/21/2009 11:00 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q408 SFMW‐32‐I2‐5 10/7/2008 9:16 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐32 (I2) I2 SFMW‐32‐I2‐5‐Q407 SFMW‐32‐I2‐5 10/1/2007 8:52 PDB GW µg/L 0.6 = 0.5 U 0.5 U 0.8 = 0.5 USFMW‐32 (I2) I2 F26A0 SFMW‐32‐I2‐5 8/28/2006 11:30 PDB GW µg/L 0.73 = 0.5 U 0.5 U 1.1 = 0.5 USFMW‐32 (I2) I2 F1NY1 SFMW‐32‐I2‐8 7/11/2005 10:05 PDB GW µg/L 1 = 0.5 U 0.21 LJ 1.9 = 0.11 LJSFMW‐32 (I2) I2 F1NY0 SFMW‐32‐I2‐5 7/11/2005 10:00 PDB GW µg/L 1 = 0.5 U 0.26 LJ 1.7 = 0.1 LJSFMW‐32 (I2) I2 F1NX9 SFMW‐32‐I2‐2 7/11/2005 9:55 PDB GW µg/L 1.3 = 0.5 U 0.26 LJ 2.1 = 0.12 LJSFMW‐32 (I2) I2 F1DR4 SFMW‐32‐I2‐8 4/20/2005 8:35 PDB GW µg/L 1 = 0.5 U 0.24 LJ 1.7 = 0.5 USFMW‐32 (I2) I2 F1DR3 SFMW‐32‐I2‐5 4/20/2005 8:32 PDB GW µg/L 1.1 = 0.5 U 0.24 LJ 1.7 = 0.5 USFMW‐32 (I2) I2 F1DR2 SFMW‐32‐I2‐2 4/20/2005 8:30 PDB GW µg/L 0.98 = 0.5 U 0.27 LJ 1.6 = 0.5 USFMW‐32 (I2) I2 F17C8 SFMW‐32‐I2 11/15/2004 14:45 LFS GW µg/L 1.7 = 0.5 U 0.32 LJ 2.7 = 0.5 USFMW‐32 (I2) I2 F17X8 SFMW‐32‐I2‐8 11/8/2004 11:45 PDB GW µg/L 0.95 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐32 (I2) I2 F17X7 SFMW‐32‐I2‐5 11/8/2004 11:40 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐32 (I2) I2 F17X6 SFMW‐32‐I2‐2 11/8/2004 11:35 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐32 (I2) I2 SFMW32‐020222 NA 2/22/2002 11:27 unknown GW µg/L 1.4 = 1 U 1 U 1.2 = 1 USFMW‐32 (I2) I2 FFZ91 NA 5/5/2000 0:00 GRN‐PUMP NMED GW µg/L 2 = 1 U 1 U 1 = 1 USFMW‐32 (I2) I2 FW546 NA 2/7/2000 0:00 unknown GW µg/L 3 = 1 U 0.8 LJ 4 = 1 USFMW‐32 (I2) I2 FGR57 NA 11/1/1999 0:00 unknown GW µg/L 2 = 1 U 1 = 1 = 1 USFMW‐32 (I2) I2 FGF52 NA 7/28/1999 0:00 unknown GW µg/L 1 = 1 U 1 U 2 = 1 USFMW‐32 (I2) I2 FX080 NA 7/27/1998 0:00 unknown GW µg/L 1 = 1 U 0.3 J 2 = 1 U
SFMW‐33 (D2) NA 5/10/2020 0:00 unknownSFMW‐33 (D2) D2 F6PM0 SFMW‐33‐D2‐5‐FD 2/13/2013 13:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F6PL9 SFMW‐33‐D2‐5 2/13/2013 13:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F6CH6 SFMW‐33‐D2‐5 8/22/2012 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F3S46 SFMW‐33‐D2‐5 2/15/2011 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW‐33‐D2‐5‐Q209 SFMW‐33‐D2‐5 4/20/2009 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW‐33‐D2‐5‐Q408 SFMW‐33‐D2‐5 10/7/2008 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW‐33‐D2‐5‐Q407 SFMW‐33‐D2‐5 10/1/2007 12:58 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F26A1 SFMW‐33‐D2‐5 8/28/2006 14:10 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1NX2 SFMW‐33‐D2‐8 7/12/2005 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1NX1 SFMW‐33‐D2‐5 7/12/2005 9:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1NW9 SFMW‐33‐D2‐2 7/12/2005 9:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1DQ5 SFMW‐33‐D2‐8 4/19/2005 11:06 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1DQ4 SFMW‐33‐D2‐5 4/19/2005 11:03 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F1DQ2 SFMW‐33‐D2‐2 4/19/2005 11:00 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F17C9 SFMW‐33‐D2 11/15/2004 9:15 LFS GW µg/L 0.5 U 0.5 U 0.5 U 0.16 LJ 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 49 OF 64
011537
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐33 (D2) D2 F17Y3 SFMW‐33‐D2‐8 11/9/2004 11:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F17Y2 SFMW‐33‐D2‐5 11/9/2004 11:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 F17Y0 SFMW‐33‐D2‐2 11/9/2004 11:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐33 (D2) D2 SFMW33‐020227 NA 2/27/2002 11:17 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐33 (D2) D2 FGS90 NA 5/1/2000 0:00 GRN‐PUMP DUKE GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐33 (D2) D2 FGF60 NA 7/28/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐33 (D2) D2 FEF70 NA 7/30/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐34 (D4) NA 5/10/2020 0:00 unknownSFMW‐34 (D4) D4 FGF65 NA 7/29/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐34 (D4) D4 FEF69 NA 7/29/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐35 (D3) NA 5/10/2020 0:00 unknownSFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐022014 SFMW‐35‐D3‐5 2/17/2014 9:38 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐0813 SFMW‐35‐D3‐5 8/13/2013 10:15 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F6PM1 SFMW‐35‐D3‐5 2/19/2013 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F6CG7 SFMW‐35‐D3‐5 8/20/2012 14:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F5GA9 SFMW‐35‐D3‐5 2/28/2012 11:28 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F3S48 SFMW‐35‐D3‐5 2/15/2011 11:56 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F3S47 SFMW‐35‐D3‐5 2/15/2011 11:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5_100201 SFMW‐35‐D3‐5 2/1/2010 14:29 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 F3B13 SFMW‐35‐D3‐5 10/26/2009 11:32 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐Q209 SFMW‐35‐D3‐5 4/21/2009 9:08 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐Q408 SFMW‐35‐D3‐5 10/7/2008 10:37 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐35 (D3) D3 SFMW‐35‐D3‐5‐Q407 SFMW‐35‐D3‐5 10/1/2007 13:23 PDB GW µg/L 0.7 = 0.5 U 0.5 U 2.3 = 0.5 USFMW‐35 (D3) D3 F26A2 SFMW‐35‐D3‐5 8/28/2006 13:30 PDB GW µg/L 0.76 = 0.5 U 0.5 U 2.8 = 0.5 USFMW‐35 (D3) D3 F1NW7 SFMW‐35‐D3‐5 7/11/2005 14:10 PDB GW µg/L 0.18 LJ 0.5 U 0.5 U 0.72 = 0.5 USFMW‐35 (D3) D3 F1NW8 SFMW‐35‐D3‐8 7/11/2005 14:10 PDB GW µg/L 0.18 LJ 0.5 U 0.5 U 0.99 = 0.5 USFMW‐35 (D3) D3 F1NW6 SFMW‐35‐D3‐2 7/11/2005 14:05 PDB GW µg/L 0.17 LJ 0.5 U 0.5 U 0.82 = 0.5 USFMW‐35 (D3) D3 F1DQ1 SFMW‐35‐D3‐8 4/18/2005 15:45 PDB GW µg/L 0.55 = 0.5 U 0.17 LJ 1.8 = 0.5 USFMW‐35 (D3) D3 F1DQ0 SFMW‐35‐D3‐5 4/18/2005 15:43 PDB GW µg/L 0.42 LJ 0.5 U 0.12 LJ 1.2 = 0.5 USFMW‐35 (D3) D3 F1DP9 SFMW‐35‐D3‐2 4/18/2005 15:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.56 = 0.5 USFMW‐35 (D3) D3 F17Y6 SFMW‐35‐D3‐8 11/9/2004 8:25 PDB GW µg/L 0.77 = 0.5 U 0.5 U 2.3 J 0.5 USFMW‐35 (D3) D3 F17Y5 SFMW‐35‐D3‐5 11/9/2004 8:20 PDB GW µg/L 0.87 = 0.5 U 0.21 LJ 2.7 = 0.5 USFMW‐35 (D3) D3 F17Y4 SFMW‐35‐D3‐2 11/9/2004 8:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.37 LJ 0.5 USFMW‐35 (D3) D3 SFMW35‐020227 NA 2/27/2002 14:49 unknown GW µg/L 1 U 1 U 1 U 3.2 = 1 USFMW‐35 (D3) D3 FW585 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 0.6 LJ 0.9 LJ 1 U 2 = 1 USFMW‐35 (D3) D3 FW559 NA 2/9/2000 0:00 unknown GW µg/L 1 U 0.8 LJ 1 U 2 = 1 USFMW‐35 (D3) D3 FGR68 NA 11/2/1999 0:00 unknown GW µg/L 0.7 LJ 0.6 LJ 1 U 2 = 1 USFMW‐35 (D3) D3 FGF82 NA 8/2/1999 0:00 unknown GW µg/L 0.6 LJ 1 = 1 U 3 = 1 USFMW‐35 (D3) D3 FQ714 NA 7/27/1998 0:00 unknown GW µg/L 0.7 J 1 = 1 U 3 = 1 USFMW‐35 (D3) D3 FX082 NA 7/27/1998 0:00 unknown GW µg/L 0.7 J 1 = 1 U 3 = 1 U
SFMW‐36 (D4) NA 5/10/2020 0:00 unknownSFMW‐36 (D4) D4 FGF94 NA 8/2/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐36 (D4) D4 FQ723 NA 7/28/1998 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐37 (I2) 5/10/2020 0:00 unknownSFMW‐37 (I2) I2 SFMW‐37‐I2‐5‐022014 SFMW‐37‐I2‐5 2/17/2014 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F6PM2 SFMW‐37‐I2‐5 2/19/2013 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 50 OF 64
011538
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐37 (I2) I2 F5GB2 SFMW‐37‐I2‐8 2/27/2012 13:44 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F5GB1 SFMW‐37‐I2‐5 2/27/2012 13:42 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F5GB0 SFMW‐37‐I2‐2 2/27/2012 13:40 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 F4EG3 SFMW‐37‐I2‐8‐Q311 8/23/2011 8:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐37 (I2) I2 F4EG2 SFMW‐37‐I2‐5‐Q311 8/23/2011 8:33 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐37 (I2) I2 F4EG1 SFMW‐37‐I2‐2‐Q311 8/23/2011 8:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USFMW‐37 (I2) I2 SFMW‐37‐I2‐8‐Q111 SFMW‐37‐I2‐8 2/16/2011 12:09 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 SFMW‐37‐I2‐5‐Q111 SFMW‐37‐I2‐5 2/16/2011 12:07 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 SFMW‐37‐I2‐2‐Q111 SFMW‐37‐I2‐2 2/16/2011 12:05 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐37 (I2) I2 FGS92 NA 5/4/2000 0:00 GRN‐PUMP NMED GW µg/L 2 = 1 U 0.6 LJ 2 = 1 USFMW‐37 (I2) I2 FGF53 NA 7/28/1999 0:00 unknown GW µg/L 2 = 1 U 0.8 LJ 3 = 1 USFMW‐37 (I2) I2 FEF77 NA 8/4/1998 0:00 unknown GW µg/L 2 = 1 U 0.8 J 3 = 0.3 JSFMW‐37 (I2) I2 FEF76 NA 8/4/1998 0:00 unknown GW µg/L 2 = 1 U 0.8 J 3 = 1 U
SFMW‐38 (D1) NA 5/10/2020 0:00 unknownSFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐022014 SFMW‐38‐D1‐5 2/18/2014 12:42 PDB GW µg/L 2.7 = 0.5 U 1 = 2.4 = 0.5 USFMW‐38 (D1) D1 F6PM4 SFMW‐38‐D1‐5‐FD 2/18/2013 10:15 PDB GW µg/L 2.9 = 0.5 U 1 = 2.3 = 0.5 USFMW‐38 (D1) D1 F6PM3 SFMW‐38‐D1‐5 2/18/2013 10:10 PDB GW µg/L 3.2 = 0.5 U 1.1 = 2.5 = 0.5 USFMW‐38 (D1) D1 F5G47 SFMW‐38‐D1‐5 2/28/2012 9:12 PDB GW µg/L 2.3 = 0.5 U 1.5 = 0.38 LJ 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q111 SFMW‐38‐D1‐5 2/14/2011 13:03 PDB GW µg/L 3.6 = 0.5 U 3.2 = 0.5 U 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5_100202 SFMW‐38‐D1‐5 2/2/2010 8:30 PDB GW µg/L 3.2 = 0.5 U 1.9 = 1.9 = 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q209 SFMW‐38‐D1‐5 4/21/2009 11:10 PDB GW µg/L 4.3 J 0.5 UJ 2.9 J 1.4 J 0.5 UJSFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q408 SFMW‐38‐D1‐5 10/7/2008 9:24 PDB GW µg/L 4.1 = 0.5 U 2 = 1.8 = 0.5 USFMW‐38 (D1) D1 SFMW‐38‐D1‐5‐Q407 SFMW‐38‐D1‐5 10/1/2007 8:44 PDB GW µg/L 5 = 0.5 U 3.5 = 0.7 = 0.5 USFMW‐38 (D1) D1 F26A3 SFMW‐38‐D1‐5 8/28/2006 11:45 PDB GW µg/L 4.4 = 0.5 U 1.8 = 1.2 = 0.5 USFMW‐38 (D1) D1 F1NY5 SFMW‐38‐D1‐8 7/11/2005 10:25 PDB GW µg/L 4.6 = 0.5 U 1.4 = 3.6 = 0.2 LJSFMW‐38 (D1) D1 F1NY4 SFMW‐38‐D1‐5 7/11/2005 10:20 PDB GW µg/L 4.7 = 0.5 U 1.4 = 3.9 = 0.2 LJSFMW‐38 (D1) D1 F1NY3 SFMW‐38‐D1‐2 7/11/2005 10:15 PDB GW µg/L 4.9 = 0.5 U 1.5 = 3.7 = 0.5 USFMW‐38 (D1) D1 F1DR8 SFMW‐38‐D1‐8 4/20/2005 9:04 PDB GW µg/L 4.7 = 0.5 U 1.4 = 3.4 = 0.5 USFMW‐38 (D1) D1 F1DR7 SFMW‐38‐D1‐5 4/20/2005 9:02 PDB GW µg/L 4.4 = 0.5 U 1.3 = 3 = 0.24 LJSFMW‐38 (D1) D1 F1DR6 SFMW‐38‐D1‐2 4/20/2005 9:00 PDB GW µg/L 4.5 = 0.5 U 1.4 = 3 = 0.5 USFMW‐38 (D1) D1 F17Y9 SFMW‐38‐D1‐8 11/8/2004 12:20 PDB GW µg/L 6.1 = 0.5 U 2 = 4 = 0.5 USFMW‐38 (D1) D1 F17Y8 SFMW‐38‐D1‐5 11/8/2004 12:15 PDB GW µg/L 5.4 = 0.5 U 1.6 = 1.7 = 0.5 USFMW‐38 (D1) D1 F17Y7 SFMW‐38‐D1‐2 11/8/2004 12:10 PDB GW µg/L 6.9 = 0.5 U 0.91 = 2.8 = 0.5 USFMW‐38 (D1) D1 SFMW38‐020301 NA 3/1/2002 11:30 unknown GW µg/L 7.2 = 1 U 2.4 = 4.6 = 1 USFMW‐38 (D1) D1 FW584 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 = 1 U 2 = 3 = 1 USFMW‐38 (D1) D1 FW545 NA 2/7/2000 0:00 unknown GW µg/L 8 = 1 U 2 = 4 = 1 U
SFMW‐39 (D2) NA 5/10/2020 0:00 unknownSFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐022014 SFMW‐39‐D2‐8 2/18/2014 12:25 PDB GW µg/L 1.9 = 0.5 U 0.7 = 0.6 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐022014 SFMW‐39‐D2‐2 2/18/2014 12:23 PDB GW µg/L 2.2 = 0.5 U 0.9 = 0.5 U 0.5 USFMW‐39 (D2) D2 F6PM6 SFMW‐39‐D2‐8 2/18/2013 9:10 PDB GW µg/L 2.8 = 0.5 U 0.69 = 2.6 = 0.5 USFMW‐39 (D2) D2 F6PM5 SFMW‐39‐D2‐2 2/18/2013 9:05 PDB GW µg/L 2.9 = 0.5 U 1.4 = 1.5 = 0.5 USFMW‐39 (D2) D2 F5G50 SFMW‐39‐D2‐8‐FD 2/28/2012 8:30 PDB GW µg/L 3.6 = 0.5 U 0.92 = 2.8 = 0.5 USFMW‐39 (D2) D2 F5G49 SFMW‐39‐D2‐8 2/28/2012 8:27 PDB GW µg/L 4.1 = 0.5 U 0.99 = 3.1 = 0.5 USFMW‐39 (D2) D2 F5G48 SFMW‐39‐D2‐2 2/28/2012 8:21 PDB GW µg/L 4.5 = 0.5 U 2 = 1.1 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q111 SFMW‐39‐D2‐8 2/14/2011 12:31 PDB GW µg/L 6 = 0.5 U 2.6 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q111 SFMW‐39‐D2‐2 2/14/2011 12:28 PDB GW µg/L 6.6 = 0.5 U 3.2 = 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 51 OF 64
011539
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐39 (D2) D2 SFMW‐39‐D2‐8_100202 SFMW‐39‐D2‐8 2/2/2010 9:18 PDB GW µg/L 6.4 = 0.5 U 3.7 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐d2‐2_100202 SFMW‐39‐D2‐2 2/2/2010 9:15 PDB GW µg/L 7 = 0.5 U 4.2 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q209 SFMW‐39‐D2‐2 4/21/2009 10:24 PDB GW µg/L 7.5 J 0.5 UJ 4.4 J 0.5 UJ 0.5 UJSFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q209 SFMW‐39‐D2‐8 4/21/2009 10:20 PDB GW µg/L 7.2 J 0.5 UJ 5.4 J 0.5 J 0.5 UJSFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q408 SFMW‐39‐D2‐8 10/6/2008 14:36 PDB GW µg/L 8.1 = 0.5 U 4.3 = 1.1 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q408 SFMW‐39‐D2‐2 10/6/2008 14:35 PDB GW µg/L 9 = 0.5 U 5.4 = 0.5 U 0.5 USFMW‐39 (D2) D2 F2RX6 SFMW‐39‐D2‐2 4/14/2008 0:00 PDB GW µg/L 9.6 = 0.5 U 4.8 = 1.7 = 0.5 USFMW‐39 (D2) D2 F2RX7 SFMW‐39‐D2‐8 4/14/2008 0:00 PDB GW µg/L 7.3 = 0.55 = 3.4 = 12 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐2‐Q407 SFMW‐39‐D2‐2 10/1/2007 9:40 PDB GW µg/L 9.8 = 0.5 U 7 = 0.5 U 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐8‐Q407 SFMW‐39‐D2‐8 10/1/2007 9:35 PDB GW µg/L 9 = 0.5 U 4.3 = 1.8 = 0.5 USFMW‐39 (D2) D2 SFMW‐39‐D2‐8_070219 SFMW‐39‐D2‐8 2/19/2007 10:30 PDB GW µg/L 8.5 JL 0.5 UJ 2 JL 6.9 JL 0.5 UJSFMW‐39 (D2) D2 SFMW‐39‐D2‐2_070219 SFMW‐39‐D2‐2 2/19/2007 10:24 PDB GW µg/L 8.1 JL 0.5 UJ 2 JL 7.4 JL 0.5 UJSFMW‐39 (D2) D2 F26A5 SFMW‐39‐D2‐8 8/28/2006 11:55 PDB GW µg/L 7.1 = 0.5 U 1.3 = 5.1 = 0.5 USFMW‐39 (D2) D2 F26A4 SFMW‐39‐D2‐2 8/28/2006 11:50 PDB GW µg/L 5.4 = 0.5 U 1 = 5.3 = 0.5 USFMW‐39 (D2) D2 F1YP7 SFMW‐39‐D2‐2 2/6/2006 12:35 PDB GW µg/L 7.7 = 0.5 U 1.6 = 9 = 0.5 USFMW‐39 (D2) D2 F1YP8 SFMW‐39‐D2‐8 2/6/2006 12:33 PDB GW µg/L 8 = 0.5 U 1.6 = 8.6 = 0.5 USFMW‐39 (D2) D2 F1NY9 SFMW‐39‐D2‐8 7/11/2005 8:40 PDB GW µg/L 8.9 = 0.5 U 2 = 17 = 0.5 USFMW‐39 (D2) D2 F1NY7 SFMW‐39‐D2‐5 7/11/2005 8:30 PDB GW µg/L 6.4 = 0.5 U 1.5 = 8.2 = 0.5 USFMW‐39 (D2) D2 F1NY6 SFMW‐39‐D2‐2 7/11/2005 8:20 PDB GW µg/L 6.5 = 0.5 U 1.5 = 9.2 = 0.5 USFMW‐39 (D2) D2 F1DS2 SFMW‐39‐D2‐8 4/20/2005 9:35 PDB GW µg/L 5.4 = 0.5 U 1.3 = 5.2 = 0.5 USFMW‐39 (D2) D2 F1DS0 SFMW‐39‐D2‐5 4/20/2005 9:32 PDB GW µg/L 5.4 = 0.5 U 1.4 = 6.4 = 0.5 USFMW‐39 (D2) D2 F1DR9 SFMW‐39‐D2‐2 4/20/2005 9:30 PDB GW µg/L 5.7 = 0.5 U 1.3 = 7.2 = 0.5 USFMW‐39 (D2) D2 F17Z3 SFMW‐39‐D2‐8 11/8/2004 9:35 PDB GW µg/L 7 Jv 0.5 UJv 2.1 Jv 7.2 Jv 0.5 USFMW‐39 (D2) D2 F17Z1 SFMW‐39‐D2‐5 11/8/2004 9:30 PDB GW µg/L 6.1 = 0.5 U 1.6 J 4.4 = 0.5 USFMW‐39 (D2) D2 F17Z0 SFMW‐39‐D2‐2 11/8/2004 9:25 PDB GW µg/L 9 = 0.5 U 1.5 = 5.8 = 0.29 LJSFMW‐39 (D2) D2 SFMW39‐020301 NA 3/1/2002 13:55 unknown GW µg/L 8.8 = 1 U 2 = 17 = 1 USFMW‐39 (D2) D2 FGT03 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 9 = 1 U 2 = 14 = 1 USFMW‐39 (D2) D2 FGS99 NA 5/4/2000 0:00 GRN‐PUMP DUKE GW µg/L 8 = 1 U 2 = 15 = 1 USFMW‐39 (D2) D2 FW542 NA 2/7/2000 0:00 unknown GW µg/L 9 = 1 U 2 = 19 = 1 U
SFMW‐40 (D3) 5/10/2020 0:00 unknownSFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐022014 SFMW‐40‐D3‐12 2/18/2014 12:41 PDB GW µg/L 4.4 = 0.5 U 0.7 = 8.5 = 0.5 USFMW‐40 (D3) D3 F6PM7 SFMW‐40‐D3‐12 2/18/2013 9:45 PDB GW µg/L 5.3 = 0.3 LJ 0.86 = 9 = 0.5 USFMW‐40 (D3) D3 F5G51 SFMW‐40‐D3‐12 2/28/2012 8:43 PDB GW µg/L 3.9 = 0.5 U 0.76 = 7.2 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐Q111 SFMW‐40‐D3‐12 2/14/2011 12:39 PDB GW µg/L 4.2 = 0.5 U 0.9 = 6.6 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12_100202‐FD SFMW‐40‐D3‐12 2/2/2010 8:55 PDB GW µg/L 4.2 = 0.5 U 1.1 = 6.3 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12_100202 SFMW‐40‐D3‐12 2/2/2010 8:55 PDB GW µg/L 4.4 = 0.5 U 1.1 = 6.6 = 0.5 USFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐Q209 SFMW‐40‐D3‐12 4/21/2009 10:30 PDB GW µg/L 4.9 J 0.5 UJ 2.1 J 5.0 J 0.5 UJSFMW‐40 (D3) D3 SFMW‐40‐D3‐12‐Q407 SFMW‐40‐D3‐12 10/1/2007 9:00 PDB GW µg/L 4.9 = 0.5 U 1.3 = 5.1 = 0.5 USFMW‐40 (D3) D3 F1NZ3 SFMW‐40‐D3‐17 7/11/2005 9:05 PDB GW µg/L 5.7 = 0.5 U 2.2 = 4.8 = 0.14 LJSFMW‐40 (D3) D3 F1NZ2 SFMW‐40‐D3‐12 7/11/2005 9:00 PDB GW µg/L 6.2 = 0.5 U 1.8 = 4.8 = 0.16 LJSFMW‐40 (D3) D3 F1NZ1 SFMW‐40‐D3‐7 7/11/2005 8:55 PDB GW µg/L 6.8 = 0.5 U 1.9 = 4.8 = 0.16 LJSFMW‐40 (D3) D3 F1NZ0 SFMW‐40‐D3‐2 7/11/2005 8:50 PDB GW µg/L 5.7 = 0.5 U 2.3 = 3.9 = 0.5 USFMW‐40 (D3) D3 F1DS6 SFMW‐40‐D3‐17 4/20/2005 10:16 PDB GW µg/L 5.7 = 0.5 U 1.7 = 3.9 = 0.5 USFMW‐40 (D3) D3 F1DS5 SFMW‐40‐D3‐12 4/20/2005 10:14 PDB GW µg/L 5.8 = 0.5 U 1.5 = 3.7 = 0.5 USFMW‐40 (D3) D3 F1DS4 SFMW‐40‐D3‐7 4/20/2005 10:12 PDB GW µg/L 5.9 = 0.5 U 1.6 = 3.8 = 0.5 USFMW‐40 (D3) D3 F1DS3 SFMW‐40‐D3‐2 4/20/2005 10:09 PDB GW µg/L 5.1 = 0.5 U 1.9 = 3.6 = 0.24 LJ
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 52 OF 64
011540
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐40 (D3) D3 F17Z7 SFMW‐40‐D3‐17 11/8/2004 10:25 PDB GW µg/L 9.1 = 0.5 U 1.2 = 4.7 = 0.5 USFMW‐40 (D3) D3 F17Z6 SFMW‐40‐D3‐12 11/8/2004 10:20 PDB GW µg/L 8.1 = 0.5 U 1 = 4.6 = 0.5 USFMW‐40 (D3) D3 F17Z5 SFMW‐40‐D3‐7 11/8/2004 10:15 PDB GW µg/L 8.4 = 0.5 U 1.1 = 4.7 = 0.5 USFMW‐40 (D3) D3 F17Z4 SFMW‐40‐D3‐2 11/8/2004 10:10 PDB GW µg/L 8 Jv 0.5 U 1.1 Jv 4.4 = 0.5 USFMW‐40 (D3) D3 SFMW40‐020305 NA 3/5/2002 9:30 unknown GW µg/L 6 = 1 U 1.7 = 5.5 = 1 USFMW‐40 (D3) D3 FW587 NA 5/2/2000 0:00 GRN‐PUMP DUKE GW µg/L 7 = 1 U 2 = 7 = 1 USFMW‐40 (D3) D3 FW555 NA 2/8/2000 0:00 unknown GW µg/L 6 = 1 U 2 = 6 = 1 U
SFMW‐41 (D3/D4) NA 5/10/2020 0:00 unknownSFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐022014 SFMW‐41‐D3/D4‐5 2/18/2014 12:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐0813 SFMW‐41‐D3/D4‐5 8/12/2013 12:00 PDB WG µg/L 0.5 U 0.5 U 0.5 U 0.8 = 0.5 USFMW‐41 (D3/D4) D3/D4 F6PM8 SFMW‐41‐D3/D4‐5 2/18/2013 9:25 PDB GW µg/L 0.5 U 0.27 LJ 0.5 U 0.36 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F6CG8 SFMW‐41‐D3/D4‐5 8/21/2012 8:08 PDB GW µg/L 0.17 LJ 0.32 LJ 0.5 U 0.75 = 0.5 USFMW‐41 (D3/D4) D3/D4 F5G52 SFMW‐41‐D3/D4‐5 2/28/2012 8:58 PDB GW µg/L 0.5 U 0.3 LJ 0.5 U 0.31 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F4EG4 SFMW‐41‐D3/D4‐5‐Q311 8/23/2011 9:00 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.1 LJ 2.0 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐Q111 SFMW‐41‐D3/D4‐5 2/14/2011 12:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 USFMW‐41 (D3/D4) D3/D4 F3LQ1 SFMW‐41‐D3/D4‐5‐Q310 9/2/2010 14:00 PDB GW µg/L 0.39 LJ 0.64 = 0.5 U 1 = 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5_100202 SFMW‐41‐D3/D4‐5 2/2/2010 9:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 1.2 = 0.5 USFMW‐41 (D3/D4) D3/D4 F3B15 SFMW‐41‐D3/D4‐5 10/26/2009 13:38 PDB GW µg/L 0.72 = 1 = 0.5 U 1.6 = 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3/D4‐5‐Q209 SFMW‐41‐D3/D4‐5 4/21/2009 10:45 PDB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSFMW‐41 (D3/D4) D3/D4 SFMW‐41‐D3‐5‐Q407 SFMW‐41‐D3‐5 10/1/2007 9:20 PDB GW µg/L 0.5 U 0.5 = 0.5 U 1.3 = 0.5 USFMW‐41 (D3/D4) D3/D4 F1NZ6 SFMW‐41‐D4‐8 7/11/2005 9:30 PDB GW µg/L 0.5 U 0.42 LJ 0.5 U 0.32 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1NZ5 SFMW‐41‐D4‐5 7/11/2005 9:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.62 = 0.5 USFMW‐41 (D3/D4) D3/D4 F1NZ4 SFMW‐41‐D4‐2 7/11/2005 9:20 PDB GW µg/L 0.5 U 0.31 LJ 0.5 U 0.56 = 0.5 USFMW‐41 (D3/D4) D3/D4 F1DS9 SFMW‐41‐D4‐8 4/20/2005 11:00 PDB GW µg/L 0.5 U 0.27 LJ 0.5 U 0.33 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1DS8 SFMW‐41‐D4‐5 4/20/2005 10:57 PDB GW µg/L 0.5 U 0.4 LJ 0.5 U 0.35 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1DS7 SFMW‐41‐D4‐2 4/20/2005 10:54 PDB GW µg/L 0.5 U 0.41 LJ 0.5 U 0.44 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1801 SFMW‐41‐D4‐8 11/8/2004 10:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.23 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F1800 SFMW‐41‐D4‐5 11/8/2004 10:50 PDB GW µg/L 0.5 U 0.23 LJ 0.5 U 0.21 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 F17Z9 SFMW‐41‐D4‐2 11/8/2004 10:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 USFMW‐41 (D3/D4) D3/D4 SFMW41‐020304 NA 3/4/2002 14:30 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐41 (D3/D4) D3/D4 FW579 NA 5/1/2000 0:00 GRN‐PUMP DUKE GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐41 (D3/D4) D3/D4 FW563 NA 2/9/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐42 unknown NA 5/10/2020 0:00 unknownSFMW‐42 unknown FW556 NA 2/8/2000 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USFMW‐42 unknown FFT54 NA 5/1/2000 0:00 BAIL GW µg/L 1 U 1 U 1 U 1 U 1 U
SFMW‐43 (D3) 5/10/2020 0:00 unknownSFMW‐43 (D3) D3 F3LQ2 SFMW‐43‐D3‐Q310 9/2/2010 11:30 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.57 = 0.5 U
SFMW‐44 (D2) 5/10/2020 0:00 unknownSFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐022014 SFMW‐44‐D2‐17 2/17/2014 12:53 PDB GW µg/L 5.7 = 0.5 U 2.4 = 10.4 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐022014 SFMW‐44‐D2‐12 2/17/2014 12:40 PDB GW µg/L 7.4 = 0.8 = 3 = 13.2 = 0.5 =SFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐0813 SFMW‐44‐D2‐17 8/12/2013 11:35 PDB WG µg/L 4.8 = 0.6 = 2 = 9 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐0813 SFMW‐44‐D2‐12 8/12/2013 11:30 PDB WG µg/L 5.3 = 0.6 = 2.1 = 9.8 = 0.5 USFMW‐44 (D2) D2 F6PN0 SFMW‐44‐D2‐17 2/19/2013 10:25 PDB GW µg/L 5.4 = 0.62 = 2.3 = 7.8 = 0.5 USFMW‐44 (D2) D2 F6PM9 SFMW‐44‐D2‐12 2/19/2013 10:20 PDB GW µg/L 5.7 = 0.59 = 2.6 = 8.5 = 0.5 USFMW‐44 (D2) D2 F6CH0 SFMW‐44‐D2‐17 8/21/2012 7:38 PDB GW µg/L 4.7 = 0.71 UM 1.8 = 7.6 = 0.5 USFMW‐44 (D2) D2 F6CG9 SFMW‐44‐D2‐12 8/21/2012 7:36 PDB GW µg/L 4.6 = 0.77 UM 1.7 = 8.0 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 53 OF 64
011541
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐44 (D2) D2 F5G54 SFMW‐44‐D2‐17 2/28/2012 12:05 PDB GW µg/L 4.5 = 0.56 = 1.9 = 9.8 = 0.5 USFMW‐44 (D2) D2 F5G53 SFMW‐44‐D2‐12 2/28/2012 11:58 PDB GW µg/L 4.1 = 0.54 = 1.7 = 9.1 = 0.5 USFMW‐44 (D2) D2 F4EG7 SFMW‐44‐D2‐17‐FD‐Q311 8/22/2011 10:58 PDB GW µg/L 6.4 = 5.0 U 2.8 LJ 13 = 2.0 USFMW‐44 (D2) D2 F4EG6 SFMW‐44‐D2‐17‐Q311 8/22/2011 10:57 PDB GW µg/L 5.4 = 5.0 U 2.1 LJ 10 = 2.0 USFMW‐44 (D2) D2 F4EG5 SFMW‐44‐D2‐12‐Q311 8/22/2011 10:56 PDB GW µg/L 5.9 = 5.0 U 2.2 LJ 11 = 2.0 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q111 SFMW‐44‐D2‐17 2/14/2011 12:00 PDB GW µg/L 5.4 = 1.5 = 1.8 = 11.2 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q111 SFMW‐44‐D2‐12 2/14/2011 11:58 PDB GW µg/L 5.6 = 1.6 = 1.9 = 11.4 = 0.5 USFMW‐44 (D2) D2 F3LQ5 SFMW‐44‐D2‐17‐Q310 8/31/2010 13:45 PDB GW µg/L 5 = 0.79 = 2 = 8.5 = 0.5 USFMW‐44 (D2) D2 F3LR1 SFMW‐44‐D2‐12‐Q310 8/31/2010 13:45 PDB GW µg/L 5.3 = 0.84 = 1.6 = 8.7 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17_100201 SFMW‐44‐D2‐17 2/1/2010 12:20 PDB GW µg/L 9.6 = 1.1 = 3.8 = 19 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12_100201 SFMW‐44‐D2‐12 2/1/2010 12:18 PDB GW µg/L 10.7 = 1.1 = 3.7 = 20.4 = 0.5 USFMW‐44 (D2) D2 F3B43 SFMW‐44‐D2‐17 10/27/2009 8:44 PDB GW µg/L 6 = 0.89 = 2.1 = 9.7 = 0.5 USFMW‐44 (D2) D2 F3B16 SFMW‐44‐D2‐12 10/26/2009 14:24 PDB GW µg/L 6.5 = 1.1 = 2.3 = 12 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q209 SFMW‐44‐D2‐17 4/20/2009 10:29 PDB GW µg/L 5.6 J 0.6 J 2.4 J 9.4 J 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q209 SFMW‐44‐D2‐12 4/20/2009 10:22 PDB GW µg/L 5.2 J 0.5 J 2.3 J 8.4 J 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q408 SFMW‐44‐D2‐17 10/6/2008 13:21 PDB GW µg/L 5.7 = 0.6 = 2.4 = 9.3 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q408 SFMW‐44‐D2‐12 10/6/2008 13:19 PDB GW µg/L 5.5 = 0.5 = 2.3 = 8.5 = 0.5 USFMW‐44 (D2) D2 F2RX8 SFMW‐44‐D2‐12 4/14/2008 0:00 PDB GW µg/L 7.3 = 0.58 = 3.2 = 12 = 0.5 USFMW‐44 (D2) D2 F2RX9 SFMW‐44‐D2‐17 4/14/2008 0:00 PDB GW µg/L 4.6 = 0.5 U 1.5 = 7.7 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐17‐Q407 SFMW‐44‐D2‐17 10/1/2007 10:13 PDB GW µg/L 6.1 = 0.6 = 3.1 = 10.1 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12‐Q407 SFMW‐44‐D2‐12 10/1/2007 10:05 PDB GW µg/L 6.1 = 0.5 = 3.1 = 9.8 = 0.5 USFMW‐44 (D2) D2 SFMW‐44‐D2‐12_070219 SFMW‐44‐D2‐12 2/19/2007 11:18 PDB GW µg/L 7.5 JL 1 JL 3 JL 13.9 JL 0.5 UJSFMW‐44 (D2) D2 SFMW‐44‐D2‐17_070219 SFMW‐44‐D2‐17 2/19/2007 11:13 PDB GW µg/L 7.2 JL 1.1 JL 3 JL 13.6 JL 0.5 UJSFMW‐44 (D2) D2 F26A7 SFMW‐44‐D2‐17 8/28/2006 12:34 PDB GW µg/L 3.7 = 0.5 U 1.8 = 6.6 = 0.5 USFMW‐44 (D2) D2 F26A6 SFMW‐44‐D2‐12 8/28/2006 12:27 PDB GW µg/L 3.7 = 0.5 U 1.7 = 6.6 = 0.5 USFMW‐44 (D2) D2 F1YW4 SFMW‐44‐D2‐12 2/6/2006 11:12 PDB GW µg/L 3.8 = 0.5 U 1.8 = 5.9 J 0.5 USFMW‐44 (D2) D2 F1YW5 SFMW‐44‐D2‐17 2/6/2006 11:10 PDB GW µg/L 4.7 = 0.5 U 2.3 = 7.3 = 0.5 USFMW‐44 (D2) D2 F1P69 SFMW‐44‐D2‐17 7/12/2005 9:44 PDB GW µg/L 6.7 = 1.2 = 3 = 13 = 0.5 USFMW‐44 (D2) D2 F1P68 SFMW‐44‐D2‐12 7/12/2005 9:40 PDB GW µg/L 5 = 0.84 = 2.3 = 9.7 J 0.5 USFMW‐44 (D2) D2 F1P66 SFMW‐44‐D2‐7 7/12/2005 9:35 PDB GW µg/L 6 = 1.1 = 2.7 = 11 = 0.5 USFMW‐44 (D2) D2 F1P65 SFMW‐44‐D2‐2 7/12/2005 9:32 PDB GW µg/L 6.4 = 0.68 = 3.1 = 12 = 0.5 USFMW‐44 (D2) D2 F1E17 SFMW‐44‐D2‐17 4/20/2005 11:22 PDB GW µg/L 4.6 = 0.83 = 1.8 = 7.5 = 0.5 USFMW‐44 (D2) D2 F1E16 SFMW‐44‐D2‐12 4/20/2005 11:17 PDB GW µg/L 4.8 = 0.88 = 1.7 = 7.7 = 0.5 USFMW‐44 (D2) D2 F1E14 SFMW‐44‐D2‐7 4/20/2005 11:12 PDB GW µg/L 4.5 = 1.2 = 1.6 = 7.5 = 0.5 USFMW‐44 (D2) D2 F1E13 SFMW‐44‐D2‐2 4/20/2005 11:09 PDB GW µg/L 4.1 = 0.55 = 1.8 = 6.8 = 0.5 USFMW‐44 (D2) D2 F1D97 SFMW‐44‐D2 4/19/2005 16:17 LFS GW µg/L 4.8 = 0.62 = 1.6 = 9.1 = 0.18 LJSFMW‐44 (D2) D2 F17D0 SFMW‐44‐D2 11/9/2004 14:30 LFS GW µg/L 7.2 = 1.3 = 2.2 = 12 = 0.5 USFMW‐44 (D2) D2 F1806 SFMW‐44‐D2‐17 11/9/2004 14:20 PDB GW µg/L 5.8 J 1.5 J 1.7 J 11 J 0.5 UJSFMW‐44 (D2) D2 F1805 SFMW‐44‐D2‐12 11/9/2004 14:15 PDB GW µg/L 5 J 1.4 J 1.7 J 11 J 0.5 UJSFMW‐44 (D2) D2 F1803 SFMW‐44‐D2‐7 11/9/2004 14:10 PDB GW µg/L 4.7 = 1.3 = 1.6 = 9.0 = 0.5 USFMW‐44 (D2) D2 F1802 SFMW‐44‐D2‐2 11/9/2004 14:05 PDB GW µg/L 4.4 = 1 = 1.6 = 7.8 = 0.5 USFMW‐44 (D2) D2 SFMW‐74 NA 4/22/2002 12:05 unknown GW µg/L 4.2 = 2.1 = 1.7 = 7.9 = 1 <SFMW‐44 (D2) D2 SFMW‐44 NA 4/22/2002 11:55 unknown GW µg/L 4 = 2.1 = 1.5 = 7.6 = 1 <
SFMW‐45 (D2) 5/10/2020 0:00 unknownSFMW‐45 (D2) D2 F6PN1 SFMW‐45‐D2‐2 2/18/2013 10:25 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.9 = 0.5 USFMW‐45 (D2) D2 F3S30 SFMW‐45‐D2‐2 2/15/2011 13:44 PDB GW µg/L 0.71 = 0.5 U 0.36 LJ 3.6 J 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 54 OF 64
011542
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐45 (D2) D2 SFMW‐45‐D2‐2‐Q407 SFMW‐45‐D2‐2 10/2/2007 9:15 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USFMW‐45 (D2) D2 F1P86 SFMW‐45‐D2‐8 7/12/2005 12:25 PDB GW µg/L 0.28 LJ 0.5 U 0.1 LJ 0.63 = 0.5 USFMW‐45 (D2) D2 F1P85 SFMW‐45‐D2‐5 7/12/2005 12:23 PDB GW µg/L 0.4 LJ 0.5 U 0.16 LJ 1.1 = 0.5 USFMW‐45 (D2) D2 F1P83 SFMW‐45‐D2‐2 7/12/2005 12:19 PDB GW µg/L 0.48 LJ 0.5 U 0.2 LJ 2.1 = 0.5 USFMW‐45 (D2) D2 F1E34 SFMW‐45‐D2‐8 4/18/2005 14:30 PDB GW µg/L 0.15 LJ 0.5 UJv 0.5 U 0.23 LJ 0.5 USFMW‐45 (D2) D2 F1E33 SFMW‐45‐D2‐5 4/18/2005 14:25 PDB GW µg/L 0.65 = 0.5 U 0.11 LJ 0.36 LJ 0.26 LJSFMW‐45 (D2) D2 F1E31 SFMW‐45‐D2‐2 4/18/2005 14:20 PDB GW µg/L 0.29 LJ 0.5 U 0.5 U 0.39 LJ 0.5 USFMW‐45 (D2) D2 F17T7 SFMW‐45‐D2‐8 11/8/2004 15:35 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.24 LJ 0.5 USFMW‐45 (D2) D2 F17T6 SFMW‐45‐D2‐5 11/8/2004 15:30 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.39 LJ 0.5 USFMW‐45 (D2) D2 F17T4 SFMW‐45‐D2‐2 11/8/2004 15:20 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.33 LJ 0.5 USFMW‐45 (D2) D2 SFMW‐45 NA 4/22/2002 15:50 unknown GW µg/L 1 < 1 < 1 < 3.1 = 1 <
SFMW‐46 (D1/D2) 5/10/2020 0:00 unknownSFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2‐022014‐FD SFMW‐46‐D1/D2‐2 2/18/2014 13:20 PDB GW µg/L 1 = 0.5 U 0.5 U 0.8 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2‐022014 SFMW‐46‐D1/D2‐2 2/18/2014 12:20 PDB GW µg/L 0.9 = 0.5 U 0.5 U 0.6 = 0.5 USFMW‐46 (D1/D2) D1/D2 F6PN2 SFMW‐46‐D1/D2‐2 2/13/2013 11:45 PDB GW µg/L 1.2 = 0.5 U 0.22 LJ 1.2 = 0.5 USFMW‐46 (D1/D2) D1/D2 F6CH1 SFMW‐46‐D1/D2‐2 8/20/2012 11:00 PDB GW µg/L 1.2 = 0.5 U 0.32 LJ 0.93 J^ 0.5 USFMW‐46 (D1/D2) D1/D2 F5G55 SFMW‐46‐D1/D2‐2 2/28/2012 12:30 PDB GW µg/L 0.94 = 0.5 U 0.5 U 0.98 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D‐2‐Q111‐FD SFMW‐46‐D1/D2‐2 2/14/2011 14:30 PDB GW µg/L 1.3 = 0.5 U 0.7 = 1 = 1.1 =SFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2‐Q111 SFMW‐46‐D1/D2‐2 2/14/2011 13:30 PDB GW µg/L 1.1 = 0.5 U 0.5 = 0.8 = 0.6 =SFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2_100201‐FD SFMW‐46‐D1/D2‐2 2/1/2010 11:43 PDB GW µg/L 1.1 = 0.5 U 0.5 U 1.2 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1/D2‐2_100201 SFMW‐46‐D1/D2‐2 2/1/2010 11:41 PDB GW µg/L 1.2 = 0.5 U 0.5 U 1.3 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46‐D1‐2‐Q408 SFMW‐46‐D1‐2 10/6/2008 13:58 PDB GW µg/L 1.9 = 0.5 U 0.6 = 1.4 = 0.5 USFMW‐46 (D1/D2) D2/D3 SFMW‐46‐D2/D3‐2‐Q407 SFMW‐46‐D2/D3‐2 10/2/2007 10:02 PDB GW µg/L 2 = 0.5 U 0.5 = 3.2 = 0.5 USFMW‐46 (D1/D2) D1/D2 F26A9 SFMW‐46‐D1/D2‐2 8/28/2006 14:35 PDB GW µg/L 0.93 = 0.5 U 0.5 U 2.6 = 0.5 USFMW‐46 (D1/D2) D1/D2 F1P91 SFMW‐46‐D1/D2‐17 7/12/2005 13:13 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 2.7 = 0.13 LJSFMW‐46 (D1/D2) D1/D2 F1P87 SFMW‐46‐D1/D2‐2 7/12/2005 13:12 PDB GW µg/L 1.4 = 0.5 U 0.27 LJ 4.7 = 0.065 LJSFMW‐46 (D1/D2) D1/D2 F1P88 SFMW‐46‐D1/D2‐7 7/12/2005 13:11 PDB GW µg/L 2.1 = 0.5 U 0.4 LJ 2.8 = 0.14 LJSFMW‐46 (D1/D2) D1/D2 F1P90 SFMW‐46‐D1/D2‐12 7/12/2005 13:11 PDB GW µg/L 2.1 = 0.5 U 0.4 LJ 2.9 = 0.14 LJSFMW‐46 (D1/D2) D1/D2 F1E39 SFMW‐46‐D1/D2‐17 4/18/2005 9:15 PDB GW µg/L 1.7 = 0.5 U 0.32 LJ 3.0 = 0.14 LJSFMW‐46 (D1/D2) D1/D2 F1E38 SFMW‐46‐D1/D2‐12 4/18/2005 9:10 PDB GW µg/L 1.8 = 0.5 U 0.36 LJ 2.9 = 0.5 USFMW‐46 (D1/D2) D1/D2 F1E36 SFMW‐46‐D1/D2‐7 4/18/2005 9:00 PDB GW µg/L 2.1 = 0.5 U 0.39 LJ 3.0 = 0.18 LJSFMW‐46 (D1/D2) D1/D2 F1E35 SFMW‐46‐D1/D2‐2 4/18/2005 8:45 PDB GW µg/L 1.5 = 0.5 U 0.29 LJ 6.0 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17W1 SFMW‐46‐D1/D2‐17 11/9/2004 14:55 PDB GW µg/L 1.8 = 0.5 U 0.33 LJ 2.4 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17W0 SFMW‐46‐D1/D2‐12 11/9/2004 14:50 PDB GW µg/L 1.9 = 0.5 U 0.38 LJ 2.8 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17T9 SFMW‐46‐D1/D2‐7 11/9/2004 14:45 PDB GW µg/L 2.2 = 0.5 U 0.39 LJ 2.9 = 0.5 USFMW‐46 (D1/D2) D1/D2 F17T8 SFMW‐46‐D1/D2‐2 11/9/2004 14:40 PDB GW µg/L 2.1 = 0.5 U 0.35 LJ 3.9 = 0.5 USFMW‐46 (D1/D2) D1/D2 SFMW‐46 NA 4/22/2002 17:40 unknown GW µg/L 1.4 = 1 < 1 < 4.9 = 1 <SFMW‐46 (D2) D1/D2 SFMW‐46‐D1/D2‐2‐0813 SFMW‐46‐D1/D2‐2 8/13/2013 8:45 PDB WG µg/L 1.1 = 0.5 U 0.5 U 1.2 = 0.5 U
SFMW‐47 (I1/I2) NA 5/10/2020 0:00 unknownSFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐022014 SFMW‐47‐I1/I2‐22 2/18/2014 8:40 PDB GW µg/L 5.3 = 0.5 U 0.7 = 20.6 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐022014 SFMW‐47‐I1/I2‐12 2/18/2014 8:37 PDB GW µg/L 4.9 = 0.5 U 0.6 = 18.5 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐0813FD SFMW‐47‐I1/I2‐12FD 8/12/2013 11:50 PDB WG µg/L 4.8 = 0.5 U 0.6 = 17.8 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐0813 SFMW‐47‐I1/I2‐22 8/12/2013 10:53 PDB WG µg/L 5.2 = 0.5 U 0.6 = 20.9 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐0813 SFMW‐47‐I1/I2‐12 8/12/2013 10:50 PDB WG µg/L 5 = 0.5 U 0.6 = 19.1 = 0.5 USFMW‐47 (I1/I2) I1/I2 F6PN4 SFMW‐47‐I1/I2‐22 2/12/2013 11:15 PDB GW µg/L 6.4 = 0.52 = 1.1 = 19 = 0.64 =SFMW‐47 (I1/I2) I1/I2 F6PN3 SFMW‐47‐I1/I2‐12 2/12/2013 11:10 PDB GW µg/L 5.4 = 0.5 U 0.67 = 18 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 55 OF 64
011543
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐47 (I1/I2) I1/I2 F6CD2 SFMW‐47‐I1/I2‐12 8/21/2012 9:46 PDB GW µg/L 4.5 = 0.5 U 0.52 = 15 = 0.5 USFMW‐47 (I1/I2) I1/I2 F6CG5 SFMW‐47‐I1/I2‐22‐FD 8/21/2012 8:44 PDB GW µg/L 4.5 = 0.5 U 0.55 = 15 = 0.5 USFMW‐47 (I1/I2) I1/I2 F6CB9 SFMW‐47‐I1/I2‐22 8/20/2012 14:06 PDB GW µg/L 4.0 = 0.13 LJ 0.61 LJ 14 = 1.0 USFMW‐47 (I1/I2) I1/I2 F5GB4 SFMW‐47‐I1/I2‐12‐FD 2/27/2012 13:15 PDB GW µg/L 3.3 = 0.5 U 0.47 LJ 13 = 0.5 USFMW‐47 (I1/I2) I1/I2 F5GB3 SFMW‐47‐I1/I2‐12 2/27/2012 12:15 PDB GW µg/L 3.4 = 0.5 U 0.52 = 15 = 0.5 USFMW‐47 (I1/I2) I1/I2 F4EG9 SFMW‐47‐I1/I2‐22‐Q311 8/22/2011 8:00 PDB GW µg/L 3.8 LJ 5.0 U 5.0 U 14 = 2.0 USFMW‐47 (I1/I2) I1/I2 F4EG8 SFMW‐47‐I1/I2‐12‐Q311 8/22/2011 8:00 PDB GW µg/L 5.6 = 5.0 U 5.0 U 20 = 2.0 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐Q11 SFMW‐47‐I1/I2‐22 2/14/2011 8:34 PDB GW µg/L 4.2 = 0.5 U 0.7 = 18.4 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐Q11 SFMW‐47‐I1/I2‐12 2/14/2011 8:25 PDB GW µg/L 4 = 0.5 U 0.6 = 16 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐22‐Q310 SFMW‐47‐I1/I2‐22‐Q310 9/8/2010 8:55 PDB GW µg/L 4.6 = 0.5 U 0.6 = 18.4 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12‐Q310 SFMW‐47‐I1/I2‐12‐Q310 9/8/2010 8:50 PDB GW µg/L 4.3 = 0.5 U 0.6 = 16.8 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1/I2‐12_100201 SFMW‐47‐I1/I2‐12 2/1/2010 12:59 PDB GW µg/L 4.3 = 0.5 U 0.7 = 17 = 0.5 USFMW‐47 (I1/I2) I1/I2 F3B77 SFMW‐47‐I1/I2‐12 10/26/2009 9:37 PDB GW µg/L 3.7 = 0.5 U 0.57 = 16 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1I2‐22‐Q209 SFMW‐47‐I1/I2‐22 4/20/2009 8:36 PDB GW µg/L 5.0 J 0.5 U 0.8 J 23.4 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1‐12‐FD‐Q209 SFMW‐47‐I1/I2‐12‐FD 4/20/2009 8:31 PDB GW µg/L 4.7 J 0.5 U 0.8 J 19.3 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I1I2‐12‐Q209 SFMW‐47‐I1/I2‐12 4/20/2009 8:30 PDB GW µg/L 4.9 J 0.5 U 0.8 J 22.2 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐22‐Q408 SFMW‐47‐I1/I2‐22 10/6/2008 10:50 PDB GW µg/L 5.6 = 0.5 U 0.9 = 25.8 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐12‐Q408 SFMW‐47‐I1/I2‐12 10/6/2008 10:48 PDB GW µg/L 5 = 0.5 U 0.8 = 22.3 = 0.5 USFMW‐47 (I1/I2) I1/I2 F2RY0 SFMW‐47‐I1/I2‐12 4/14/2008 0:00 PDB GW µg/L 6.5 = 0.5 U 1 = 33 = 0.5 USFMW‐47 (I1/I2) I1/I2 F2RY1 SFMW‐47‐I1/I2‐22 4/14/2008 0:00 PDB GW µg/L 6.8 = 0.5 U 1.1 = 33 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐12‐Q407 SFMW‐47‐I2‐12 10/1/2007 8:31 PDB GW µg/L 5.8 = 0.5 U 1.1 = 26.2 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐22‐Q407 SFMW‐47‐I2‐22 10/1/2007 8:29 PDB GW µg/L 6 = 0.5 U 1 = 28.2 = 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐12_070219 SFMW‐47‐I2‐12 2/19/2007 8:13 PDB GW µg/L 6.2 JL 0.5 UJ 1.1 JL 35.4 JL 0.5 UJSFMW‐47 (I1/I2) I1/I2 SFMW‐47‐I2‐22_070219 SFMW‐47‐I2‐22 2/19/2007 8:13 PDB GW µg/L 6.5 JL 0.5 UJ 1.1 JL 37 JL 0.5 UJSFMW‐47 (I1/I2) I1/I2 F26B1DL SFMW‐47‐I2‐22 8/29/2006 7:55 PDB GW µg/L 21 =SFMW‐47 (I1/I2) I1/I2 F26B1 SFMW‐47‐I2‐22 8/29/2006 7:55 PDB GW µg/L 3.9 = 0.5 U 0.58 = 0.5 USFMW‐47 (I1/I2) I1/I2 F26B0DL SFMW‐47‐I2‐12 8/29/2006 7:50 PDB GW µg/L 2.7 = 19 =SFMW‐47 (I1/I2) I1/I2 F26B0 SFMW‐47‐I2‐12 8/29/2006 7:50 PDB GW µg/L 0.5 U 0.65 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1YR3DL SFMW‐47‐I2‐22 2/6/2006 8:29 PDB GW µg/L 27 =SFMW‐47 (I1/I2) I1/I2 F1YR3 SFMW‐47‐I2‐22 2/6/2006 8:29 PDB GW µg/L 5.9 = 0.5 U 1 = 0.5 USFMW‐47 (I1/I2) I1/I2 F1YR2DL SFMW‐47‐I2‐12 2/6/2006 8:27 PDB GW µg/L 28 =SFMW‐47 (I1/I2) I1/I2 F1YR2 SFMW‐47‐I2‐12 2/6/2006 8:27 PDB GW µg/L 5.6 = 0.5 U 1 = 0.5 USFMW‐47 (I1/I2) I1/I2 F1NX8DL SFMW‐47‐I2‐27 7/13/2005 8:53 PDB GW µg/L 29 =SFMW‐47 (I1/I2) I1/I2 F1NX8 SFMW‐47‐I2‐27 7/13/2005 8:53 PDB GW µg/L 6.2 = 0.5 U 1.1 = 0.18 LJSFMW‐47 (I1/I2) I1/I2 F1NX7DL SFMW‐47‐I2‐22 7/13/2005 8:51 PDB GW µg/L 30 =SFMW‐47 (I1/I2) I1/I2 F1NX7 SFMW‐47‐I2‐22 7/13/2005 8:51 PDB GW µg/L 6.5 = 0.5 U 1.2 = 0.18 LJSFMW‐47 (I1/I2) I1/I2 F1NX6DL SFMW‐47‐I2‐17 7/13/2005 8:50 PDB GW µg/L 29 =SFMW‐47 (I1/I2) I1/I2 F1NX6 SFMW‐47‐I2‐17 7/13/2005 8:50 PDB GW µg/L 6.3 = 0.5 U 1.2 = 0.16 LJSFMW‐47 (I1/I2) I1/I2 F1NX3DL SFMW‐47‐I2‐2 7/13/2005 8:49 PDB GW µg/L 27 =SFMW‐47 (I1/I2) I1/I2 F1NX5DL SFMW‐47‐I2‐12 7/13/2005 8:49 PDB GW µg/L 28 =SFMW‐47 (I1/I2) I1/I2 F1NX3 SFMW‐47‐I2‐2 7/13/2005 8:49 PDB GW µg/L 6.3 = 0.5 U 1.2 = 0.16 LJSFMW‐47 (I1/I2) I1/I2 F1NX5 SFMW‐47‐I2‐12 7/13/2005 8:49 PDB GW µg/L 6.5 = 0.5 U 1.3 = 0.5 USFMW‐47 (I1/I2) I1/I2 F1NX4DL SFMW‐47‐I2‐7 7/13/2005 8:47 PDB GW µg/L 27 =SFMW‐47 (I1/I2) I1/I2 F1NX4 SFMW‐47‐I2‐7 7/13/2005 8:47 PDB GW µg/L 6.2 = 0.5 U 1.2 = 0.17 LJSFMW‐47 (I1/I2) I1/I2 F1DR1 SFMW‐47‐I2‐27 4/19/2005 9:54 PDB GW µg/L 9.6 = 0.5 U 1.7 = 63 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1DR0 SFMW‐47‐I2‐22 4/19/2005 9:52 PDB GW µg/L 10 = 0.5 U 1.9 = 65 J 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 56 OF 64
011544
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSFMW‐47 (I1/I2) I1/I2 F1DQ9 SFMW‐47‐I2‐17 4/19/2005 9:50 PDB GW µg/L 10 = 0.5 U 1.8 = 65 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1DQ8 SFMW‐47‐I2‐12 4/19/2005 9:48 PDB GW µg/L 7.6 = 0.5 U 1.5 = 51 J 0.5 USFMW‐47 (I1/I2) I1/I2 F1DQ7DL SFMW‐47‐I2‐7 4/19/2005 9:46 PDB GW µg/L 48 =SFMW‐47 (I1/I2) I1/I2 F1DQ7 SFMW‐47‐I2‐7 4/19/2005 9:46 PDB GW µg/L 7.5 = 0.5 U 1.5 = 0.19 LJSFMW‐47 (I1/I2) I1/I2 F1DQ6 SFMW‐47‐I2‐2 4/19/2005 9:44 PDB GW µg/L 7.4 = 0.5 U 1.5 = 48 J 0.21 LJSFMW‐47 (I1/I2) I1/I2 F17M6 SFMW‐47‐I2‐27 11/9/2004 13:20 PDB GW µg/L 6.9 = 0.5 U 1.2 = 50 J 0.5 USFMW‐47 (I1/I2) I1/I2 F17M5 SFMW‐47‐I2‐22 11/9/2004 13:17 PDB GW µg/L 6.7 = 0.5 U 1.2 = 49 J 0.37 LJSFMW‐47 (I1/I2) I1/I2 F17M4 SFMW‐47‐I2‐17 11/9/2004 13:15 PDB GW µg/L 7.4 = 0.5 U 1.3 U 55 J 0.5 USFMW‐47 (I1/I2) I1/I2 F17M3 SFMW‐47‐I2‐12 11/9/2004 13:11 PDB GW µg/L 7.8 = 0.5 U 1.3 = 56 J 0.5 USFMW‐47 (I1/I2) I1/I2 F17M2 SFMW‐47‐I2‐7 11/9/2004 13:07 PDB GW µg/L 7.8 = 0.5 U 1.3 = 49 J 0.25 LJSFMW‐47 (I1/I2) I1/I2 F17M1 SFMW‐47‐I2‐2 11/9/2004 13:06 PDB GW µg/L 7 = 0.5 U 1.3 = 45 J 0.5 USFMW‐47 (I1/I2) I1/I2 SFMW‐47 NA 4/25/2002 0:00 unknown GW µg/L 8.4 = 1 < 1.7 = 48 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47AT‐5 NA 4/16/2002 10:30 unknown GW µg/L 11.3 = 1 < 3 = 50.9 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47‐AT‐4 NA 4/15/2002 9:10 unknown GW µg/L 10.9 = 1 < 2.6 = 55.7 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47‐AT‐3 NA 4/14/2002 13:15 unknown GW µg/L 10.5 = 1 < 2.8 = 66.3 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47AT‐2 NA 4/13/2002 13:45 unknown GW µg/L 9.8 = 1 < 2.2 = 54.3 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW‐47AT‐1 NA 4/13/2002 10:40 unknown GW µg/L 9.6 = 1 < 2.3 = 53.5 = 1 <SFMW‐47 (I1/I2) I1/I2 SFMW47 B dev‐020311 NA 3/11/2002 17:45 unknown GW µg/L 8.7 = 1 U 2 = 58 = 1 USFMW‐47 (I1/I2) I1/I2 SFMW47 P dev‐020311 NA 3/11/2002 17:15 unknown GW µg/L 5.1 = 1 U 1 = 33 = 1 U
SHB‐4/WellNo. 1 (S) NA 5/10/2020 0:00 unknownSHB‐4/WellNo. 1 (S) S FW881 NA 12/10/1996 0:00 unknown GW µg/L 0.6 J 1 U 0.6 J 1 U NDSHB‐4/WellNo. 1 (S) S 309302‐6 NA 8/31/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 5 ND 10 NDSHB‐4/WellNo. 1 (S) S 930901‐7 NA 8/31/1993 0:00 unknown GW µg/L 0.8 = <0.2 0.6 = 0.5 = NDSHB‐4/WellNo. 1 (S) S FX016 NA 8/31/1993 0:00 unknown GW µg/L 0.8 J 1 U 1 = 0.7 J NDSHB‐4/WellNo. 1 (S) S FQ928 NA 5/20/1993 0:00 unknown GW µg/L 2 J 10 U 10 U ND
SP‐1 NA 5/10/2020 0:00 unknownSP‐1 D2 FAP_SP‐1‐18032013 FAP_SP‐1‐18032013 3/18/2013 14:12 GRAB GW µg/L 1.4 = 0.5 U 0.5 U 3.7 = 0.5 USP‐1 D2 FAP_SP‐1‐18032013‐FD FAP_SP‐1‐18032013‐FD 3/18/2013 14:11 GRAB GW µg/L 1.4 = 0.5 U 0.5 U 3.6 = 0.5 USP‐1 D2 FAP_SP‐1‐20022013‐FD FAP_SP‐1‐20022013‐FD 2/20/2013 14:55 GRAB GW µg/L 1.4 = 0.5 U 0.5 U 3.6 = 0.5 USP‐1 D2 FAP_SP‐1‐20022013 FAP_SP‐1‐20022013 2/20/2013 14:50 GRAB GW µg/L 1.4 = 0.5 U 0.5 U 3.6 = 0.5 USP‐1 D2 FAP_SP‐1‐21012013‐FD FAP_SP‐1‐21012013‐FD 1/21/2013 9:00 GRAB GW µg/L 1.9 = 0.5 U 0.6 = 4.9 = 0.5 USP‐1 D2 FAP_SP‐1‐21012013 FAP_SP‐1‐21012013 1/21/2013 8:45 GRAB GW µg/L 2.0 = 0.5 U 0.6 = 5.1 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 12/19/2012 0:00 GRAB GW µg/L 1.8 = 0.5 U 0.6 = 4.7 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 11/19/2012 0:00 GRAB GW µg/L 2.1 = 0.5 U 0.6 = 6.1 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 10/18/2012 0:00 GRAB GW µg/L 1.7 = 0.5 U 0.5 U 5 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 9/18/2012 0:00 GRAB GW µg/L 0.84 = 0.5 U 0.21 LJ 1.8 = 0.5 USP‐1 D2 FAP_SP‐1‐06082012FD FAP_SP‐1‐06082012FD 8/6/2012 14:20 GRAB GW µg/L 2.1 = 0.5 U 0.5 U 6.0 = 0.5 USP‐1 D2 FAP_SP‐1‐06082012 FAP_SP‐1‐06082012 8/6/2012 14:10 GRAB GW µg/L 2.3 = 0.5 U 0.5 U 6.0 = 0.5 USP‐1 D2 FAP_SP‐1‐07162012FD FAP_SP‐1‐07162012FD 7/16/2012 10:05 GRAB GW µg/L 1.9 = 0.5 U 0.5 = 4.6 = 0.5 USP‐1 D2 FAP_SP‐1‐07162012 FAP_SP‐1‐07162012 7/16/2012 10:00 GRAB GW µg/L 1.8 = 0.5 U 0.5 U 4.6 = 0.5 USP‐1 D2 F5Y06 SP‐1‐19062012‐FD 6/19/2012 9:07 GRAB GW µg/L 2.6 = 0.5 U 0.76 = 5.9 = 0.5 USP‐1 D2 F5Y05 SP‐1‐19062012 6/19/2012 9:05 GRAB GW µg/L 2.7 = 0.5 U 0.69 = 6.3 = 0.5 USP‐1 D2 F5W97 SP‐1‐22052012‐FD 5/22/2012 14:08 GRAB GW µg/L 1.9 = 0.5 U 0.60 = 4.9 = 0.5 USP‐1 D2 F5W95 SP‐1‐22052012 5/22/2012 14:05 GRAB GW µg/L 1.9 = 0.5 U 0.56 = 5.0 = 0.5 USP‐1 D2 F5LL7 FAP_SP‐1‐04162012‐FD 4/16/2012 12:59 GRAB GW µg/L 2.7 = 0.5 U 0.75 = 6.9 = 0.5 USP‐1 D2 F5LL6 FAP_SP‐1‐04162012 4/16/2012 12:58 GRAB GW µg/L 2.6 = 0.5 U 0.71 = 6.5 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 57 OF 64
011545
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSP‐1 D2 F5HF1 FAP_SP‐1‐19032012‐DU 3/19/2012 14:27 GRAB GW µg/L 2.3 = 0.083 LJ 0.55 = 5.9 = 0.5 USP‐1 D2 F5HF0 FAP_SP‐1‐19032012 3/19/2012 14:26 GRAB GW µg/L 2.1 = 0.084 LJ 0.53 = 6 = 0.5 USP‐1 D2 FAP_SP‐1‐27022012‐FD FAP_SP‐1‐27022012‐FD 2/28/2012 15:02 GRAB GW µg/L 1.8 = 0.5 U 0.5 = 4.7 = 0.5 USP‐1 D2 FAP_SP‐1‐27022012 FAP_SP‐1‐27022012 2/28/2012 15:02 GRAB GW µg/L 1.9 = 0.5 U 0.5 = 4.7 = 0.5 USP‐1 D2 F5AJ7 FAP_SP‐1‐16012012 1/16/2012 0:00 GRAB GW µg/L 2.3 = 0.086 LJ 0.66 = 6.3 = 0.5 USP‐1 D2 F5AJ8RE2 FAP_SP‐1‐16012012‐DU 1/16/2012 0:00 GRAB GW µg/L 2.5 J^ 0.1 LJ 0.84 J^ 9.2 J^ 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 11/22/2011 0:00 GRAB GW µg/L 2.1 = 0.5 U 2.0 U 4.9 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 10/17/2011 0:00 GRAB GW µg/L 1.6 = 0.5 U 2.0 U 3.8 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 10/17/2011 0:00 GRAB GW µg/L 2.0 = 0.5 U 2.0 U 4.6 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 9/19/2011 0:00 GRAB GW µg/L 1.8 = 0.5 U 2.0 U 4 = 0.5 USP‐1 D2 F4EH1 SP‐1_DUP‐Q311 8/22/2011 15:15 GRAB GW µg/L 3.1 LJ 5.0 U 5.0 U 8.9 = 2.0 USP‐1 D2 F4EH0 SP‐1‐Q311 8/22/2011 15:10 GRAB GW µg/L 3.3 LJ 5.0 U 5.0 U 8.9 = 2.0 USP‐1 D2 FAP_SP‐1‐24032011‐DUP FAP_SP‐1 3/24/2011 9:35 GRAB GW µg/L 2.6 = 0.5 U 0.8 = 6.1 = 0.5 USP‐1 D2 FAP_SP‐1‐24032011 FAP_SP‐1 3/24/2011 9:32 GRAB GW µg/L 2.7 = 0.5 U 0.8 = 6.2 = 0.5 USP‐1 D2 FAP_SP‐1_Q111_DUP FAP_SP‐1 2/14/2011 14:18 GRAB GW µg/L 2.2 J 0.5 UJ 0.6 J 6.1 J 0.5 UJSP‐1 D2 FAP_SP‐1_Q111 FAP‐SP‐1 2/14/2011 14:17 GRAB GW µg/L 2.2 J 0.5 UJ 0.7 J 6.1 J 0.5 UJSP‐1 D2 FAP_SP‐1_110125‐DUP FAP‐SP‐1 1/25/2011 13:35 GRAB GW µg/L 2.2 = 0.5 U 0.6 = 5.4 = 0.5 USP‐1 D2 FAP_SP‐1_110125 FAP‐SP‐1 1/25/2011 13:30 GRAB GW µg/L 2.2 = 0.5 U 0.7 = 5.6 = 0.5 USP‐1 D2 F3RM3 FAP_SP‐1 12/14/2010 10:00 GRAB GW µg/L 2.4 = 0.5 U 0.69 = 5.9 = 0.5 USP‐1 D2 F3RM2 FAP_SP‐1 12/14/2010 9:58 GRAB GW µg/L 2.3 = 0.5 U 0.66 = 5.7 = 0.5 USP‐1 D2 FAP_SP‐1 DUP FAP_SP‐1DUP 9/23/2010 13:41 GRAB GW µg/L 1.5 = 0.5 U 0.5 U 4.2 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1_23092010 9/23/2010 13:40 GRAB GW µg/L 1.6 = 0.5 U 0.5 U 4.4 = 0.5 USP‐1 D2 FAP_SP‐1‐Q310‐DUP FAP_SP‐1‐Q310‐DUP 9/7/2010 15:01 GRAB GW µg/L 1.9 = 0.5 U 0.6 = 5.0 = 0.5 USP‐1 D2 FAP_SP‐1‐Q310 FAP_SP‐1‐Q310 9/7/2010 14:58 GRAB GW µg/L 2.1 = 0.5 U 0.6 = 5.2 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 6/22/2010 0:00 GRAB GW µg/L 1.9 = 0.5 U 0.6 = 5.3 = 0.5 USP‐1 D2 FAP_SP‐1 FAP_SP‐1 3/18/2010 0:00 GRAB GW µg/L 1.8 = 0.5 U 0.6 = 5 = 0.5 USP‐1 D2 FAP_SP‐1_100201_DUP FAP_SP‐1 2/1/2010 15:36 GRAB GW µg/L 2.2 = 0.5 U 0.6 = 5.6 = 0.5 USP‐1 D2 FAP_SP‐1_100201 FAP_SP‐1 2/1/2010 15:35 GRAB GW µg/L 2.0 = 0.5 U 0.6 = 5.5 = 0.5 USP‐1 D2 FAP SP‐1 FAP_SP‐1 11/30/2009 0:00 GRAB GW µg/L 1.8 = 0.5 U 0.5 U 4.9 = 0.5 USP‐1 D2 FAP SP‐1‐Q409 FAP_SP‐1 10/28/2009 0:00 GRAB GW µg/L 1.8 = 0.5 U 0.51 = 4.8 = 0.5 USP‐1 D2 FAP SP‐1‐Q309 FAP_SP‐1 7/6/2009 0:00 GRAB GW µg/L 2.5 = 0.5 U 0.9 = 7.6 = 0.5 USP‐1 D2 FAP SP‐1‐Q209 FAP_SP‐1 4/20/2009 0:00 GRAB GW µg/L 3.0 = 0.5 U 1. = 7.7 = 0.5 USP‐1 D2 FAP SP‐1 090212 FAP_SP‐1 2/12/2009 0:00 GRAB GW µg/L 3.2 = 0.5 U 1.1 = 7.3 = 0.5 USP‐1 D2 FAP SP‐1 081111 FAP_SP‐1 11/11/2008 0:00 GRAB GW µg/L 3.0 = 0.5 U 1. = 7.8 = 0.5 USP‐1 D2 FAP SP‐1 080707 FAP_SP‐1 7/7/2008 0:00 GRAB GW µg/L 3.4 = 0.5 U 1.2 = 8.9 = 0.5 USP‐1 D2 FAP SP‐1 080414 FAP_SP‐1 4/14/2008 0:00 GRAB GW µg/L 4.6 = 0.5 U 1.5 = 11.0. = 0.5 USP‐1 D2 FAP SP‐1 080218 FAP_SP‐1 2/18/2008 0:00 GRAB GW µg/L 3.8 = 0.5 U 1.4 = 9.7 = 0.5 USP‐1 D2 FAP SP‐1 071029 FAP_SP‐1 10/28/2007 0:00 GRAB GW µg/L 4.4 = 0.5 U 1.5 = 11.4 = 0.5 USP‐1 D2 FAP SP‐1 070823 FAP_SP‐1 8/23/2007 0:00 GRAB GW µg/L 4.1 = 0.5 U 1.5 = 10.0 = 0.5 USP‐1 D2 FAP SP‐1 070602 FAP_SP‐1 6/2/2007 0:00 GRAB GW µg/L 4.1 = 0.5 U 1.5 = 10.2 = 0.5 USP‐1 D2 FAP SP‐1 C07 FAP_SP‐1 2/20/2007 0:00 GRAB GW µg/L 4.1 = 0.5 U 1.4 = 12.0 = 0.5 USP‐1 D2 FAP SP‐1 B07 FAP_SP‐1 2/20/2007 0:00 GRAB GW µg/L 4.2 = 0.5 U 1.5 = 12.0 = 0.5 USP‐1 D2 FAP SP‐1 A07 FAP_SP‐1 2/19/2007 0:00 GRAB GW µg/L 4.2 = 0.5 U 1.6 = 12.1 = 0.5 USP‐1 D2 FAP SP‐1 061016 FAP_SP‐1 10/16/2006 0:00 GRAB GW µg/L 4.6 = 0.5 U 1.7 = 11.6 = 0.5 USP‐1 D2 FAP SP‐1 0600816 FAP_SP‐1 8/16/2006 0:00 GRAB GW µg/L 5.6 = 0.5 U 1.9 = 13.6 = 0.5 USP‐1 D2 FAP SP‐1 0600719 FAP_SP‐1 7/19/2006 0:00 GRAB GW µg/L 5.6 = 0.5 U 2.1 = 13.4 = 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 58 OF 64
011546
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSP‐1 D2 FAP SP‐1 060524 FAP_SP‐1 5/24/2006 0:00 GRAB GW µg/L 4.7 = 0.5 U 1.9 = 12.8 = 0.5 USP‐1 D2 FAP SP‐1 060329 FAP_SP‐1 3/29/2006 0:00 GRAB GW µg/L 5.0 = 0.5 U 1. = 12.0 = 0.5 USP‐1 D2 FAP SP‐1 060308 FAP_SP‐1 3/8/2006 0:00 GRAB GW µg/L 4.3 = 0.5 U 1.5 = 13.0 = 0.5 USP‐1 D2 FAP SP‐1 060127 FAP_SP‐1 1/27/2006 0:00 GRAB GW µg/L 4.6 = 0.5 U 2.3 = 12.0 = 0.5 USP‐1 D2 FAP SP‐1 060109 FAP_SP‐1 1/9/2006 0:00 GRAB GW µg/L 6.0 = 0.5 U 2.5 = 13.0 = 0.5 USP‐1 D2 FAP SP‐1 051130 FAP_SP‐1 11/30/2005 0:00 GRAB GW µg/L 5.0 = 0.5 U 1.4 = 11.0 = 0.5 USP‐1 D2 FAP Infl 102505 FAP_SP‐1 10/25/2005 0:00 GRAB GW µg/L 6.6 = 0.5 U 2.7 = 14.0 = 0.5 USP‐1 D2 FAP Infl 102105 FAP_SP‐1 10/21/2005 0:00 GRAB GW µg/L 5.3 = 0.5 U 2.2 = 12.0 = 0.5 USP‐1 D2 FAP Infl 101905 FAP_SP‐1 10/19/2005 0:00 GRAB GW µg/L 5.7 = 0.5 U 2.1 = 12.0 = 0.5 USP‐1 D2 ASTP INFLUENT FAP_SP‐1 3/17/2005 0:00 GRAB GW µg/L 6.0 = 0.5 U 2.4 = 15.0 = 0.5 USP‐1 D2 ASTP INFLUENT FAP_SP‐1 2/22/2005 0:00 GRAB GW µg/L 5.6 = 0.5 U 2.4 = 14.0 = 0.5 USP‐1 D2 Q105ASTPINFLUENT2 FAP_SP‐1 1/5/2005 0:00 GRAB GW µg/L 5.3 = 0.5 U 2.4 = 12.0 = 0.5 USP‐1 D2 Q105ASTPINFLUENT4 FAP_SP‐1 1/5/2005 0:00 GRAB GW µg/L 5.4 = 0.5 U 2.4 = 12.0 = 0.5 USP‐1 D2 Q105ASTPINFLUENT3 FAP_SP‐1 1/5/2005 0:00 GRAB GW µg/L 4.9 = 0.5 U 2.3 = 13.0 = 0.5 USP‐1 D2 Q105ASTPINFLUENT1 FAP_SP‐1 1/5/2005 0:00 GRAB GW µg/L 5.7 = 0.5 U 2.5 = 13.0 = 0.5 U
SP‐5 5/10/2020 0:00 unknownSP‐5 NA FAP_SP‐5‐18032013 FAP_SP‐5‐18032013 3/18/2013 14:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐27022012 FAP_SP‐5‐20022013 2/20/2013 14:55 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5AJ6 FAP_SP‐5‐21012013 1/21/2013 9:15 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 12/19/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 11/19/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 10/18/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 9/18/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐06082012 FAP_SP‐5‐06082012 8/6/2012 14:35 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐07162012 FAP_SP‐5‐07162012 7/16/2012 10:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5Y07 SP‐5‐19062012 6/19/2012 9:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5W96 SP‐5‐22052012 5/22/2012 14:10 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5LL8 FAP_SP‐5‐04162012 4/16/2012 13:01 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5HF2 FAP_SP‐5‐19032012 3/19/2012 14:17 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐27022012 FAP_SP‐5‐27022012 2/28/2012 15:20 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F5AJ6 FAP_SP‐5‐16012012 1/16/2012 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 12/19/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 11/22/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 10/17/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 10/17/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 9/19/2011 0:00 GRAB GW µg/L 2.0 U 0.5 U 2.0 U 2.0 U 0.5 USP‐5 NA F4EH2 SP‐5‐Q311 8/22/2011 15:20 GRAB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 USP‐5 NA FAP SP‐5 FAP_SP‐5 7/18/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 6/20/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 5/24/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 FAP_SP‐5 4/18/2011 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5‐24032011 FAP_SP‐5 3/24/2011 9:40 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP_SP‐5_Q111 FAP_SP‐5 2/14/2011 14:20 GRAB GW µg/L 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJ 0.5 UJSP‐5 NA FAP_SP‐5_110125 FAP_SP‐5 1/25/2011 13:40 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA F3RM4 FAP_SP‐5 12/14/2010 9:55 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP‐SP‐5 FAP‐SP‐5 9/23/2010 13:46 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 59 OF 64
011547
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSP‐5 NA FAP_SP‐5‐Q310 SP_SP‐5‐Q310 9/7/2010 15:04 GRAB GW µg/L 2.1 = 0.5 U 0.6 = 5.0 = 0.5 USP‐5 NA FAP SP‐5‐Q409 b FAP_SP‐5 10/28/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5‐Q309 b FAP_SP‐5 7/6/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 20090603 b FAP_SP‐5 6/3/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5‐Q209 bc FAP_SP‐5 4/20/2009 0:00 GRAB GW µg/L 2.9 = 0.5 U 0.8 = 7.3 = 0.5 USP‐5 NA FAP SP‐5 090212 b FAP_SP‐5 2/12/2009 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 081111 b FAP_SP‐5 11/11/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080707 b FAP_SP‐5 7/7/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080707‐DUP b FAP_SP‐5 7/7/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080414 b FAP_SP‐5 4/14/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080414‐DUP b FAP_SP‐5 4/14/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 080218 b FAP_SP‐5 2/18/2008 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 071029 b FAP_SP‐5 10/28/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 070823‐DUP FAP_SP‐5 8/23/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 070823 b FAP_SP‐5 8/23/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 070602 b FAP_SP‐5 6/2/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 B07 b FAP_SP‐5 2/20/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 C07 b FAP_SP‐5 2/20/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 A07 b FAP_SP‐5 2/19/2007 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 061016 FAP_SP‐5 10/16/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 0600816 FAP_SP‐5 8/16/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 0600719 FAP_SP‐5 7/19/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 060524 FAP_SP‐5 5/24/2006 0:00 GRAB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 USP‐5 NA FAP SP‐5 060329c FAP_SP‐5 3/29/2006 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP SP‐5 060308c FAP_SP‐5 3/8/2006 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP SP‐5 060127c FAP_SP‐5 1/27/2006 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP SP‐5 051130c FAP_SP‐5 11/30/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP Treated 102505c FAP_SP‐5 10/25/2005 0:00 GRAB GW µg/L 0.8 J 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP Treated 102105c FAP_SP‐5 10/21/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FAP Treated 101905c FAP_SP‐5 10/19/2005 0:00 GRAB GW µg/L 0.7 J 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA FFL. BAG FILTER DISCHARGE Cb FAP_SP‐5 3/17/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA ASTP EFFLUENTb FAP_SP‐5 2/22/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT1b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT2b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT3b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT4b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 USP‐5 NA Q105ASTPEFFLUENT5b FAP_SP‐5 1/5/2005 0:00 GRAB GW µg/L 1.0 U 0.5 U 1.0 U 1.0 U 0.5 U
SPSC/Ice Plant NA 5/10/2020 0:00 unknownSPSC/Ice Plant unknown OR‐93‐2055 NA 8/26/1993 0:00 unknown GW µg/L 1 U 0.85 J 1 U 1 U NDSPSC/Ice Plant unknown OR‐93‐1776 NA 7/28/1993 0:00 unknown GW µg/L 2.5 = 1 = 1 U 3.6 = NDSPSC/Ice Plant unknown notassigned‐7 NA 4/26/1989 0:00 unknown GW µg/L ND ND ND NDSPSC/Ice Plant unknown notassigned‐6 NA 8/20/1987 0:00 unknown GW µg/L ND ND ND NDSPSC/Ice Plant unknown notassigned‐5 NA 12/3/1986 0:00 unknown GW µg/L ND ND ND ND
SPSC‐MW1 unknown NA 5/10/2020 0:00 unknownSPSC‐MW1 unknown 309302‐1 NA 8/31/1993 0:00 unknown GW µg/L 3 J 5 ND 3 J 3 J 10 NDSPSC‐MW1 unknown 930901‐3 NA 8/31/1993 0:00 unknown GW µg/L 3.3 = <0.2 3 = 2.8 = ND
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 60 OF 64
011548
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSPSC‐MW1 unknown 91158604 NA 11/7/1989 0:00 unknown GW µg/L 5.4 = <0.2 3.3 = ND
SPSC‐MW2 unknown NA 5/10/2020 0:00 unknownSPSC‐MW2 unknown 930901‐2 NA 8/31/1993 0:00 unknown GW µg/L 3 = 1.4 = 2.6 = 2.6 = NDSPSC‐MW2 unknown 309302‐7 NA 8/31/1993 0:00 unknown GW µg/L 5 ND 1 J 5 ND 5 ND NDSPSC‐MW2 unknown 930902‐16 NA 8/30/1993 0:00 unknown GW µg/L 3.6 = 0.6 = 1.7 = 4.9 = <0.2SPSC‐MW2 unknown 00153701 NA 1/3/1990 0:00 unknown GW µg/L 15 = 0.7 = 11 = ND
SPSC‐MW3 unknown NA 5/10/2020 0:00 unknownSPSC‐MW3 unknown FGF79 NA 7/30/1999 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USPSC‐MW3 unknown FQ857 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USPSC‐MW3 unknown FW882 NA 12/10/1996 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U NDSPSC‐MW3 unknown 309302‐2 NA 8/31/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 3 J 10 NDSPSC‐MW3 unknown 930901‐1 NA 8/31/1993 0:00 unknown GW µg/L 2.5 = 1.1 = 2.4 = 3.9 = NDSPSC‐MW3 unknown 930902‐1 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐MW3 unknown 930902‐15 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐MW3 unknown 309302‐10 NA 8/30/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 5 ND NDSPSC‐MW3 unknown 00153702 NA 1/3/1990 0:00 unknown GW µg/L 1.4 = <0.2 1.1 = ND
SPSC‐MW4 unknown NA 5/10/2020 0:00 unknownSPSC‐MW4 unknown FFT53 NA 5/1/2000 0:00 BAIL GW µg/L 2 = 1 U 0.8 LJ 3 = 1 USPSC‐MW4 unknown FW554 NA 2/8/2000 0:00 unknown GW µg/L 1 = 1 U 0.7 LJ 3 = 1 USPSC‐MW4 unknown FGR70 NA 11/2/1999 0:00 unknown GW µg/L 2 = 1 U 1 = 2 = 1 USPSC‐MW4 unknown FGF61 NA 7/28/1999 0:00 unknown GW µg/L 1 = 1 U 0.6 LJ 3 = 1 USPSC‐MW4 unknown FQ809 NA 11/5/1997 0:00 unknown GW µg/L 1 = 1 U 0.7 J 3 = 1 USPSC‐MW4 unknown FW883 NA 12/10/1996 0:00 unknown GW µg/L 2 = 0 U 1 = 3 = NDSPSC‐MW4 unknown 931025‐2 NA 10/13/1993 0:00 unknown GW µg/L 1.1 = <0.2 0.6 = 1.7 = <0.2SPSC‐MW4 unknown 309302‐4 NA 8/31/1993 0:00 unknown GW µg/L 2 J 5 ND 5 ND 1 J 10 NDSPSC‐MW4 unknown 930901‐6 NA 8/31/1993 0:00 unknown GW µg/L 2.8 = 0.4 = <0.2 1.7 = NDSPSC‐MW4 unknown 930901‐4 NA 8/31/1993 0:00 unknown GW µg/L 6.2 = <0.2 2.4 = 24 = ND
SPSC‐MW5 unknown NA 5/10/2020 0:00 unknownSPSC‐MW5 unknown FQ810 NA 11/5/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 USPSC‐MW5 unknown 309302‐3 NA 8/31/1993 0:00 unknown GW µg/L 2 J 5 ND 5 ND 5 = 10 NDSPSC‐MW5 unknown 930901‐5 NA 8/31/1993 0:00 unknown GW µg/L 3.3 = <0.2 2.1 = 4.9 = NDSPSC‐MW5 unknown 930902‐3 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐MW6 unknown NA 5/10/2020 0:00 unknownSPSC‐MW6 unknown 930901‐10 NA 9/1/1993 0:00 unknown GW µg/L 7 = <0.2 2.5 = 26 = NDSPSC‐MW6 unknown 309302‐5 NA 8/31/1993 0:00 unknown GW µg/L 6 = 5 ND 5 ND 24 = 10 NDSPSC‐MW6 unknown 930902‐5 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐MW7 unknown NA 5/10/2020 0:00 unknownSPSC‐MW7 unknown 930901‐8 NA 8/31/1993 0:00 unknown GW µg/L 1.9 = 0.7 = 1.5 = <0.2 NDSPSC‐MW7 unknown 309302‐9 NA 8/31/1993 0:00 unknown GW µg/L <5 <5 <5 <5 NDSPSC‐MW7 unknown 930902‐2 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐MW7 unknown 930902‐8 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
SPSC‐MW8 unknown NA 5/10/2020 0:00 unknownSPSC‐MW8 unknown 930902‐9 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2SPSC‐MW8 unknown 930902‐6 NA 8/30/1993 0:00 unknown GW µg/L 0.2 = <0.2 <0.2 <0.2 <0.2
SPSC‐MWD unknown NA 5/10/2020 0:00 unknownSPSC‐MWD unknown 930902‐7 NA 8/30/1993 0:00 unknown GW µg/L 0.3 = <0.2 <0.2 0.3 = <0.2
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 61 OF 64
011549
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodSPSC‐W13 unknown NA 5/10/2020 0:00 unknown
SPSC‐W13 unknown 930902‐11 NA 8/31/1993 0:00 unknown GW µg/L 0.3 = <0.2 <0.2 0.2 = <0.2SPSC‐W14 unknown NA 5/10/2020 0:00 unknown
SPSC‐W14 unknown 930902‐12 NA 8/31/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐W15 unknown NA 5/10/2020 0:00 unknown
SPSC‐W15 unknown 930902‐4 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2SPSC‐W18 unknown NA 5/10/2020 0:00 unknown
SPSC‐W18 unknown 930902‐10 NA 8/30/1993 0:00 unknown GW µg/L 2 = 0.3 = 0.7 = 2.3 = <0.2SPSC‐W19 unknown NA 5/10/2020 0:00 unknown
SPSC‐W19 unknown 612323‐02 NA 12/11/1996 0:00 unknown GW µg/L <1 <1 <1 <1 NDSPSC‐W19 unknown 930902‐14 NA 8/30/1993 0:00 unknown GW µg/L 0.6 = <0.2 <0.2 0.7 = <0.2SPSC‐W19 unknown 309302‐11 NA 8/30/1993 0:00 unknown GW µg/L 5 ND 5 ND 5 ND 5 ND ND
SPSC‐W20 unknown NA 5/10/2020 0:00 unknownSPSC‐W20 unknown 930902‐13 NA 8/30/1993 0:00 unknown GW µg/L <0.2 <0.2 <0.2 <0.2 <0.2
St. Jos. Supply unknown NA 5/10/2020 0:00 unknownSt. Jos. Supply unknown FGT01 NA 5/4/2000 0:00 OTHER GW µg/L 2 = 1 U 1 U 6 = 1 USt. Jos. Supply unknown FR847 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 3 = 1 USt. Jos. Supply unknown FR848 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 3 = 1 USt. Jos. Supply unknown FR849 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 3 = 1 USt. Jos. Supply unknown FR850 NA 5/13/1998 0:00 unknown GW µg/L 1 = 0.6 J 1 U 4 = 1 USt. Jos. Supply unknown FR839 NA 5/12/1998 0:00 unknown GW µg/L 2 = 1 U 1 U 10 = 1 USt. Jos. Supply unknown FR842 NA 5/12/1998 0:00 unknown GW µg/L 2 = 1 U 1 U 10 = 1 USt. Jos. Supply unknown FR840 NA 5/12/1998 0:00 unknown GW µg/L 3 = 1 U 1 U 10 = 1 USt. Jos. Supply unknown OR‐93‐3175 NA 12/8/1993 0:00 unknown GW µg/L 1 U 1.6 = 1 U 1 = NDSt. Jos. Supply unknown OR‐93‐2954 NA 11/17/1993 0:00 unknown GW µg/L 1 U 1.5 = 1 U 0.9 J NDSt. Jos. Supply unknown notassigned‐8 NA 12/3/1986 0:00 unknown GW µg/L ND ND ND ND
WB‐01 (I1/I2) NA 5/10/2020 0:00 unknownWB‐01 (I1/I2) I1/I2 F6PN5 WB‐01‐I1/I2‐27 2/18/2013 0:00 PDB GW µg/L 0.96 = 0.5 U 0.11 LJ 1.7 = 0.5 UWB‐01 (I1/I2) I1/I2 F6PN6 WB‐01‐I1/I2‐27‐FD 2/18/2013 0:00 PDB GW µg/L 1 = 0.5 U 0.5 U 2 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G60 WB‐01‐I1/I2‐27 2/27/2012 11:55 PDB GW µg/L 0.74 = 0.5 U 0.5 U 1.2 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G59 WB‐01‐I1/I2‐22 2/27/2012 11:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G57 WB‐01‐I1/I2‐17 2/27/2012 11:50 PDB GW µg/L 0.53 = 0.5 U 0.5 U 0.8 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G56 WB‐01‐I1/I2‐12 2/27/2012 11:48 PDB GW µg/L 0.49 LJ 0.5 U 0.5 U 0.78 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G61 WB‐01‐I1/I2‐7 2/27/2012 11:45 PDB GW µg/L 0.41 LJ 0.5 U 0.5 U 0.74 = 0.5 UWB‐01 (I1/I2) I1/I2 F5G58 WB‐01‐I1/I2‐2 2/27/2012 11:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.58 = 0.5 UWB‐01 (I1/I2) I1/I2 F4EI1 WB‐01‐I1/I2‐27‐Q311 8/22/2011 8:02 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.8 LJ 2.0 UWB‐01 (I1/I2) I1/I2 F4EI0 WB‐01‐I1/I2‐22‐Q311 8/22/2011 8:01 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.6 LJ 2.0 UWB‐01 (I1/I2) I1/I2 F4EH8 WB‐01‐I1/I2‐17‐Q311 8/22/2011 8:00 PDB GW µg/L 1.1 LJ 5.0 U 5.0 U 1.6 LJ 2.0 UWB‐01 (I1/I2) I1/I2 F4EH7 WB‐01‐I1/I2‐12‐Q311 8/22/2011 7:55 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F4EI3 WB‐01‐I1/I2‐7‐FD‐Q311 8/22/2011 7:52 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F4EI2 WB‐01‐I1/I2‐7‐Q311 8/22/2011 7:51 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F4EH9 WB‐01‐I1/I2‐2‐Q311 8/22/2011 7:50 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐01 (I1/I2) I1/I2 F3S54 WB‐01‐I1/I2‐27 2/18/2011 8:55 PDB GW µg/L 0.32 LJ 0.5 U 0.5 U 0.47 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S55 WB‐01‐I1/I2‐22 2/18/2011 8:53 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.27 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S53 WB‐01‐I1/I2‐22 2/18/2011 8:50 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.28 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S52 WB‐01‐I1/I2‐17 2/18/2011 8:48 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.25 LJ 0.5 U
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 62 OF 64
011550
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodWB‐01 (I1/I2) I1/I2 F3S51 WB‐01‐I1/I2‐12 2/18/2011 8:45 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.29 LJ 0.5 UWB‐01 (I1/I2) I1/I2 F3S50 WB‐01‐I1/I2‐7 2/18/2011 8:43 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UWB‐01 (I1/I2) I1/I2 F3S49 WB‐01‐I1/I2‐2 2/18/2011 8:41 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 U 0.5 UWB‐01 (I1/I2) I FX090 NA 5/3/2000 0:00 GRN‐PUMP NMED GW µg/L 4 = 1 U 0.8 LJ 4 = 1 UWB‐01 (I1/I2) I FGF39 NA 7/27/1999 0:00 unknown GW µg/L 4 = 1 U 0.8 LJ 4 = 1 UWB‐01 (I1/I2) I FQ845 NA 11/3/1997 0:00 unknown GW µg/L 4 = 1 U 0.9 J 5 = 1 UWB‐01 (I1/I2) I 9705043‐2 NA 5/19/1997 0:00 unknown GW µg/L 2.8 = 1 ND 1 ND 3.6 = ND
WB‐01 (S) NA 5/10/2020 0:00 unknownWB‐01 (S) S FX088 NA 5/2/2000 0:00 BAIL GW µg/L 0.6 LJ 1 U 1 U 0.5 LJ 1 UWB‐01 (S) S FQ843 NA 11/3/1997 0:00 unknown GW µg/L 0.6 J 1 U 1 U 0.6 J 1 UWB‐01 (S) S 9705043‐1 NA 5/19/1997 0:00 unknown GW µg/L 1 ND 1 ND 1 ND 1 ND ND
WB‐02 (I1/I2) NA 5/10/2020 0:00 unknownWB‐02 (I1/I2) I1/I2 F6PN7 WB‐02‐I1/I2‐27 2/18/2013 12:35 PDB GW µg/L 0.57 = 0.5 U 0.5 U 0.81 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G66 WB‐02‐I1/I2‐27 2/27/2012 11:15 PDB GW µg/L 0.51 = 0.5 U 0.5 U 0.77 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G65 WB‐02‐I1/I2‐22 2/27/2012 11:12 PDB GW µg/L 0.46 LJ 0.5 U 0.5 U 0.71 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G63 WB‐02‐I1/I2‐17 2/27/2012 11:09 PDB GW µg/L 0.44 LJ 0.5 U 0.5 U 0.76 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G62 WB‐02‐I1/I2‐12 2/27/2012 11:06 PDB GW µg/L 0.5 LJ 0.5 U 0.5 U 0.73 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G68 WB‐02‐I1/I2‐7‐FD 2/27/2012 11:04 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.77 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G67 WB‐02‐I1/I2‐7 2/27/2012 11:02 PDB GW µg/L 0.59 = 0.5 U 0.5 U 1.1 = 0.5 UWB‐02 (I1/I2) I1/I2 F5G64 WB‐02‐I1/I2‐2 2/27/2012 10:59 PDB GW µg/L 0.53 = 0.5 U 0.5 U 0.77 = 0.5 UWB‐02 (I1/I2) I1/I2 F4EI8 WB‐02‐I1/I2‐27‐Q311 8/22/2011 8:55 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐02 (I1/I2) I1/I2 F4EI7 WB‐02‐I1/I2‐22‐Q311 8/22/2011 8:50 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐02 (I1/I2) I1/I2 F4EI5 WB‐02‐I1/I2‐17‐Q311 8/22/2011 8:45 PDB GW µg/L 0.88 LJ 5.0 U 5.0 U 1.1 LJ 2.0 UWB‐02 (I1/I2) I1/I2 F4EI4 WB‐02‐I1/I2‐12‐Q311 8/22/2011 8:40 PDB GW µg/L 5.0 U 5.0 U 5.0 U 5.0 U 2.0 UWB‐02 (I1/I2) I1/I2 F4EI9 WB‐02‐I1/I2‐7‐Q311 8/22/2011 8:35 PDB GW µg/L 5.0 U 5.0 U 5.0 U 2.1 LJ 2.0 UWB‐02 (I1/I2) I1/I2 F4EI6 WB‐02‐I1/I2‐2‐Q311 8/22/2011 8:30 PDB GW µg/L 5.0 U 5.0 U 5.0 U 1.1 LJ 2.0 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐27‐Q111 WB‐02‐I1/I2‐27 2/16/2011 13:01 PDB GW µg/L 0.6 = 0.5 U 0.5 U 1 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐22‐Q111 WB‐02‐I1/I2‐22 2/16/2011 12:59 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.7 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐17‐Q111 WB‐02‐I1/I2‐17 2/16/2011 12:57 PDB GW µg/L 0.5 = 0.5 U 0.5 U 0.6 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐12‐Q111 WB‐02‐I1/I2‐12 2/16/2011 12:55 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐7‐Q111 WB‐02‐I1/I2‐7 2/16/2011 12:54 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.6 = 0.5 UWB‐02 (I1/I2) I1/I2 WB‐02‐I1/I2‐2‐Q111 WB‐02‐I1/I2‐2 2/16/2011 12:51 PDB GW µg/L 0.5 U 0.5 U 0.5 U 0.5 = 0.5 UWB‐02 (I1/I2) I FGF40 NA 7/27/1999 0:00 unknown GW µg/L 4 = 1 U 0.6 LJ 4 = 1 UWB‐02 (I1/I2) I FQ841 NA 11/3/1997 0:00 unknown GW µg/L 4 = 1 U 1 U 4 = 1 UWB‐02 (I1/I2) I 9705043‐4 NA 5/19/1997 0:00 unknown GW µg/L 3.1 = 1 ND 1 ND 3.4 = ND
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 63 OF 64
011551
TABLE 2Summary of Historical Chlorinated Solvents Detected in Groundwater, December 1986 through February 2014Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
1,2‐DCE (cis & trans)
cis‐1,2‐DCE PCE trans‐1,2‐DCE TCE Vinyl Chloride
70 70 5 100 5 2bMatrix UnitRemediation Goals (MCLs) µg/L
Station IDAquifer Zone
Zonea Sample IDPDB interval where
applicable Date Collected Sampling MethodWB‐02 (S) NA 5/10/2020 0:00 unknown
WB‐02 (S) S FQ839 NA 11/3/1997 0:00 unknown GW µg/L 1 U 1 U 1 U 1 U 1 UWB‐02 (S) S 9705043‐3 NA 5/19/1997 0:00 unknown GW µg/L 1 ND 1 ND 1 ND 1 ND ND
5/10/2020 0:00 unknownNotes:
µg/L = micrograms per liter
DCE = Dichloroethylene
PCE = Perchloroethylene (tetrachloroethylene)
TCE = Trichloroethylene
MCL = maximum contaminant level
PDB = passive diffusion bag
LFS = low‐flow sampling
Unknown = unknown sample interval
GW = groundwater
DL = Diluted sample
U = Not detected
= = Detected concentration
J = Estimated concentration
v = Low biased. Actual concentration may be higher
than the reported concentration.
^ = High biased. Actual concentration may be lower
than the reported concentration.
L = Reported concentration is below the contract‐required
quantitation limit.
* = See Long‐term Monitoring Plan (included in Volume 1 of
the 100% Remedial Design) for description of the Aquifer Zones.
** = The Record of Decision does not list a remediation goal for
vinyl chloride. Value is the MCL.
Bold results are concentrations above the laboratory reporting limits.
Yellow‐highlighted results are concentrations above the remedial action goals.
FAP_2014_LTM_SEMI_TABLE 2ES050514041759SPB PAGE 64 OF 64
011552
FAP_2014_LTM_SEMI_TABLE 3ES050514041759SPB PAGE 1 OF 1
TABLE 3Trichloroethylene Concentrations and Passive Diffusion Bag Selection at Monitor Wells New to the Long-term Monitoring ProgramFruit Avenue Plume Superfund Site, Albuquerque, New Mexico
PDB Interval 2 PDB Interval 5 PDB Interval 8
TCE (µg/L) TCE (µg/L) TCE (µg/L)
2/15/2011 0.5 U 0.5 U 0.74
8/22/2011 4.7 JL 3.5 JL 11
2/27/2012 3.3 8 5.8
8/20/2012 11 3.3 8.7
2/13/2013 3.9 10 6
8/12/2013 6.6 3.6 9.2
2/17/2014 2.6 2.8 6.6
Sampling Date PDB Interval 2 PDB Interval 5 PDB Interval 8
TCE (µg/L) TCE (µg/L) TCE (µg/L)
10/26/2009 0.5 U 0.5 U 0.5 U
9/7/2010 0.5 U 5.2 0.5 U
8/22/2011 5 U 5 U 5 U
8/21/2012 10 0.5 U 0.5 U
2/13/2013 0.5 U 0.5 U 0.5 U
8/12/2013 0.5 U 0.5 U 0.5 U
2/18/2014 0.5 U 0.5 U 0.5 U
Notes:µg/L = micrograms per literFD = field duplicate sampleLTM = long-term monitoringMW = Monitor WellPDB = Passive Diffusion BagTCE = TrichloroethyleneU = Not detectedJL = Estimated concentration below the contract-required quantitation limit.
SFMW-28 (I2)
McDonalds (D2)
Sampling Date
011553
Figures
011554
FIGURES
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FAP_2014_LTM_SEMI_FIGURES ES050514041759SPB
011555
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\SITE_MAP_FEB_2014.MXD FLONDON 5/1/2014 10:15:11 AM
FIGURE 1LTM Program, Monitor Well LocationsFruit Avenue Plume Superfund SiteAlbuquerque, NM
Legend
Presumed Source Area
Extraction Well
Air Stripper Treatment Plant
Injection Well
RailroadMonitor Wells
pruc
e S
t
Silver Ave
Copper Ave
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
Silver Ave
Marquette Pl
Granite AveMarble Ave
Oak
St
Syc
Map
le S
t
Spru
ce S
t
Hig
h S
t
Gold Ave
Legion
Tijeras Ave
Luna
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Manzano Ct
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
cam
ore
St
SpruceS
7th
St
Ced
ar S
t
Edith
Blvd
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
8th
St
Enci
no P
l
7th
St
Tijeras Ave
Iron Ave
1st S
3rd
S t
4th
St
St
11th
St
Fruit Ave Lomas Blvd
5th
St
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank DM-01
(S)
DM-05 (S)
DM-06(I1/I2)
DM-07(I1/I2)
DM-08(I1/I2)
DM-09 (S)
DM-10(S)
DM-11(S)
DM-12(I1/I2)
DM-13(S/I1/I2/D1)
HSM-I2-4(I2)
HSM-I2-5 (I2)
McDonald’s(D2)
MNW-1(I2)
MNW-10 (I1/I2)
MNW-11(I1/I2/D1/D2)
MNW-12(I1/I2/D1/D2)
MNW-13(D1/d2/D3/D4)
MNW-14(I2/D1/D2)
MNW-2(I2)
MNW-3 (D1/D2/D3)
MNW-4(D1/D2/D3)
MNW-5(D1/D2/D3/D4)
MNW-6(D1/D2/D3)
MNW-7(D4)
MNW-8 (I1)
MNW-8(I2)
MNW-9(I1/I2/D1/D2)
SFMW-01(S)
SFMW-03 (S)
SFMW-07 (S)
SFMW-10 (I2)SFMW-11(S)
SFMW-12(I1)
SFMW-13 (I2)
SFMW-14 (D1) SFMW-15 (S)
SFMW-16(I1)
SFMW-17 (I2)
SFMW-18 (I1)
SFMW-20(I1)
SFMW-21(I2)
SFMW-22 (D1)SFMW-23 (D2)
SFMW-24(S) SFMW-25
(I1/I2)
SFMW-26(I2)
SFMW-27 (I2)
SFMW-28(I2)
SFMW-31 (I2)
SFMW-32 (I2)
SFMW-33(D2)
SFMW-34(D4)
SFMW-35(D3)
SFMW-36(D4)
SFMW-37(I2)
SFMW-38(D1)
SFMW-39(D2)
SFMW-40(D3)
SFMW-41(D3/D4)
SFMW-43(I1)
SFMW-44(D2)
SFMW-45(D2)
SFMW-46(D1/D2)
SFMW-47(I1/I2)
SPSC-MW19(S)
SPSC-MW5 (S)
SPSC-W13(S)
MNW-15(D1/D2/D3)
WB-01(I1/I2)
WB-02 (I1/I2)
MNW-16(D1/D2/D3/D4)
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
?
? 5
5
I2/D1E-I1D2E-I3
D2E-P1
0 300 600150 Feet
Aquifer Zones:S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011556
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-01 (S)4921.93
DM-05 (S)4921.31
DM-09 (S)4918.51
DM-10 (S)4917.55
DM-11 (S)4924.94
DM-13 (S)4921.07
SFMW-01 (S)4922.77
SFMW-03 (S)4921.23
SFMW-07 (S)4923.35
SFMW-11 (S)4926.89
SFMW-15 (S)4919.84
SFMW-24 (S)4919.32
SPSC-MW19 (S)4914.76
SPSC-MW5 (S)4917.5
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4925
4915
4920 I2/D1E-I1
D2E-I3D2E-P1
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_S.MXD FLONDON 5/1/2014 11:25:51 AM
LegendS Zone Monitor WellOther Site Monitor WellExtraction WellAir Stripper Treatment PlantInjection WellWater Level Elevation Contour - (Dashed Where Inferred)
Inferred Direction of Groundwater FlowRailroadPipelinesPresumed Source Area
0 300 600150 Feet
1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 2
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011557
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-06 (I1/I2)4916.55
DM-07 (I1/I2)4917.12
DM-08 (I1/I2)4917.33
DM-12 (I1/I2)4925.95
DM-13 (I1)4921.83
MNW-10 (I1)4928.48
MNW-11 (I1)4933.61
MNW-12 (I1)4933.67
MNW-8 (I1)4930.11
MNW-9 (I1)4931.59
SFMW-12 (I1)4926.93
SFMW-16 (I1)4920.62
SFMW-18 (I1)4923.79
SFMW-20 (I1)4911.31
SFMW-25 (I1/I2)4918.34
SFMW-43 (I1)4903.13
SFMW-47 (I1/I2)4921.63
WB-02 (I1/I2)4927.62
WB-01 (I1/I2)4928.76
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4915 4910 4905
4930
4920
4925
I2/D1E-I1D2E-I3
D2E-P1
LegendI1 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Water Level Elevation Contour - (Dashed Where Inferred)
Inferred Direction of Groundwater Flow
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_I1.MXD FLONDON 5/1/2014 11:31:56 AM
0 300 600150 Feet
1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 3
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011558
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-06 (I1/I2)4916.55
DM-07 (I1/I2)4917.12
DM-08 (I1/I2)4917.33
DM-12 (I1/I2)4925.95
HSM-I2-4 (I2)4925.58
HSM-I2-5 (I2)4924.04MNW-1 (I2)
4929.68
MNW-10 (I2)4928.51
MNW-11 (I2)4933.62
MNW-12 (I2)4933.64
MNW-14 (I2)4926.75
MNW-2 (I2)4925.02
MNW-8 (I2)4930.27
MNW-9 (I2)4931.65
SFMW-10 (I2)4925.57
SFMW-13 (I2)4926.98
SFMW-17 (I2)4922.03
SFMW-21 (I2)4911.5
SFMW-25 (I1/I2)4918.34
SFMW-26 (I2)4917.98
SFMW-27 (I2)4926.16
SFMW-28 (I2)4923.8
SFMW-31 (I2)4903.56
SFMW-32 (I2)4904.65
SFMW-37 (I2)4914.36
SFMW-47 (I1/I2)4921.63
WB-02 (I1/I2)4927.62
WB-01 (I1/I2)4928.76
DM-13 (I2)4922.77
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4915
4910
49054930
49204925
I2/D1E-I1
D2E-I3
D2E-P1
LegendI2 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour - (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_I2.MXD FLONDON 4/29/2014 1:36:09 PM
0 300 600150 Feet
1. Water levels are in feet above Mean Sea Level (MSL).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 4
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011559
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-13 (D1)4925.55
MNW-11 (D1)4933.59
MNW-12 (D1)4933.68
MNW-13 (D1)4907.30
MNW-14 (D1)4928.48
MNW-3 (D1)4914.70
MNW-4 (D1)4907.00
MNW-5 (D1)4910.35
MNW-6 (D1)4912.16
MNW-9 (D1)4931.55
SFMW-14 (D1)4927.17
SFMW-22 (D1)4912.39
SFMW-38 (D1)4908.33
SFMW-46 (D1/D2)4906.67
MNW-15 (D1)4892.54
MNW-16 (D1)4907.44
4930
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4925
4920
4915
4910
4905
4900 4895
I2/D1E-I1
D2E-I3
D2E-P1
LegendD1 Zone Monitor Well
Other Site Monitor Well
Air Stripper Treatment Plant
Injection Well
Extraction Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D1.MXD FLONDON 5/1/2014 11:34:12 AM
FIGURE 5
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
0 300 600150 Feet
1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011560
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
McDonald’s (D2)4914.35
MNW-11 (D2)4933.57
MNW-12 (D2)4933.64
MNW-13 (D2)4907.55MNW-14 (D2)
4928.88
MNW-3 (D2)4913.85
MNW-4 (D2)4906.94
MNW-5 (D2)4910.65
MNW-6 (D2)4912.3
MNW-9 (D2)4931.71
SFMW-23 (D2)4912.24
SFMW-33 (D2)4914.87
SFMW-39 (D2)4908.3
SFMW-44 (D2)4910.09
SFMW-45 (D2)4909.14
SFMW-46 (D1/D2)4906.67
MNW-15 (D2)4904.28
MNW-16 (D2)4907.91
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4915
4910
4905
4930
4920
4925
I2/D1E-I1
D2E-I3
D2E-P1
LegendD2 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour - (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D2.MXD FLONDON 5/1/2014 11:35:05 AM
0 300 600150 Feet
1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 6
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011561
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
MNW-13 (D3)4908.03
MNW-3 (D3)4913.11 MNW-4 (D3)
4907.34
MNW-5 (D3)4911.15
MNW-6 (D3)4912.45
SFMW-35 (D3)4911.3
SFMW-40 (D3)4907.87 MNW-15 (D3)
4904.52
MNW-16 (D3)4908.16
SFMW-41 (D3/D4)4907.48
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4905
4910
I2/D1E-I1D2E-I3
D2E-P1
LegendD3 Zone Monitor WellOther Site Monitor Well
Extraction Well
Air Stripper Treatment Plant
Injection Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour - (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D3.MXD FLONDON 5/1/2014 11:36:30 AM
0 300 600150 Feet
FIGURE 7
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011562
Maloof
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
MNW-13 (D4)4908.51
MNW-5 (D4)4911.04
MNW-7 (D4)4910.77
SFMW-34 (D4)4911.43
SFMW-36 (D4)4910.58
MNW-16 (D4)4908.55
SFMW-41 (D3/D4)4907.48
4910
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
4910
I2/D1E-I1
D2E-I3
D2E-P1
LegendD4 Zone Monitor Well
Other Site Monitor Well
Air Stripper Treatment Plant
Injection Well
Extraction Well
Inferred Direction of Groundwater Flow
Water Level Elevation Contour (Dashed Where Inferred)
Railroad
Pipelines
Presumed Source Area
DVR \\MNUSTRICTGFS01\PROJECTS\FRUITAVENUE_345406\MAPFILES\FEB_2013\FA_GW_ELE_D4.MXD FLONDON 5/1/2014 3:49:00 PM
0 300 600150 Feet
1. Water levels are in feet above mean sea level (amsl).2. Water level contour interval is 5 feet.3. Water level data contoured by hand by triangulation with linear interpolation with consideration for known site hydrogeology. Horizontal flow is assumed based on homogeneous and isotropic conditions.4. * - Unable to locate well.5. NM - Water level not measured.
FIGURE 8
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
S - Shallow Aquifer Zone - Above 4,912 ft above mean sea level (amsl)I1 - Intermediate 1 Aquifer Zone - 4,912 ft to 4,872 ft amslI2 - Intermediate 2 Aquifer Zone - 4,872 ft to 4,847 ft amslD1 - Deep 1 Aquifer Zone - 4,847 ft to 4,752 ft amslD2 - Deep 2 Aquifer Zone - 4,752 ft to 4,647 ft amslD3 - Deep 3 Aquifer Zone - 4,647 ft to 4,552 ft amslD4 - Deep 4 Aquifer Zone - 4,552 ft to 4,400 ft amsl
011563
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\FA_TCE_S.MXD FLONDON 5/1/2014 8:48:15 AM
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Granite Ave
Silver Ave
Copper Ave
11th
St
Tijeras Av
d Pl
Don
Cip
riano
Ct
Slate Ave
Marquette Pl
Granite AveMarble Ave
Oak
St
Spru
ce S
t
Tijeras Ave
Luna
Bl v
d
1st S
t
Elm
St
h S
t
Gold Ave
6th
St
Medical Arts Ave
Rid
Slate Ave
Page Ave
Manzano Ct
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
7th
St
Ced
ar S
t
Edith
Blvd
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
8th
St
Encin
o Pl
7th
St
Tijeras Ave
1st S
t
3rd
S t
4th
St
11th
St
Fruit Ave Lomas Blvd
5th
St
hS
t
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quilin
o C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-05 (S)PCE 0.7 =TCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
DM-09 (S)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
I2/D1E-I1
D2E-I3
D2E-P1
011564
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\FA_TCE_I1.MXD FLONDON 5/1/2014 9:10:37 AM
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Granite Ave
Silver Ave
Copper Ave
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
1
Marquette Pl
Granite AveMarble Ave
Oak
St
Sycam
Forr
e
Map
le S
t
Spru
ce S
t
Legion R
Tijeras Ave
Luna
Bl v
d
1st S
t
Elm
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Manzano Ct
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
SpruceSt
7th
St
St
Edith
Blv
d
Hig
h S
t
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
8th
St
Enci
no P
l
7th
St
Tijeras Ave
1st S
t
3rd
St
4th
St
11th
St
Fruit Ave
12th
St
Wa
Lomas Blvd
5th
St
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
h B
lvd
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Lead Ave
SH 4
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank DM-06 (I1/I2)
PCE 0.5 UTCE 0.9 =cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
DM-07 (I1/I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
DM-08 (I1/I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-16 (I1)PCE 0.5 UTCE 5.8 =cis-DCE 0.8 =trans-DCE 0.5 UVC 0.5 U
SFMW-18 (I1)PCE 0.5 UTCE 1.8 =cis-DCE 0.9 =trans-DCE 0.5 UVC 0.5 U
SFMW-20 (I1)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-47 (I1/I2)PCE 0.5 UTCE 20.6 =cis-DCE 5.3 =trans-DCE 0.7 =VC 0.5 U
SFMW-25 (I1)PCE 0.5 UTCE 4.6 =cis-DCE 2.3 =trans-DCE 0.9 =VC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
15
10
5
I2/D1E-I1D2E-I3
D2E-P1
011565
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\FA_TCE_I2.MXD FLONDON 5/1/2014 11:52:03 AM
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
ruce
St
Silver Ave
Copper Ave
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
Silver Ave
Marquette Pl
Granite AveMarble Ave
Oak
St
Sycam
o
Map
le S
t
Spru
ce S
t
Hig
h S
t
Gold Ave
Legion R
Tijeras Ave
Luna
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Manzano Ct
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
amor
e S
t
Spruce St
7th
St
Ced
ar S
t
Edith
Blv
d
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
8th
St
Enci
no P
l
7th
St
eras Ave
Iron A
1st S
t
3rd
St
4th
St
St
11th
St
Fruit Ave Lomas Blvd
5th
St
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
DM-06 (I1/I2)PCE 0.5 UTCE 0.9 =cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
DM-07 (I1/I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
DM-08 (I1/I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
HSM-I2-5 (I2)PCE 0.5 UTCE 17.9 =cis-DCE 5.9 =trans-DCE 0.8 =VC 0.5 U
MNW-1 (I2)PCE 0.5 UTCE 19 =cis-DCE 4.1 =trans-DCE 1 =VC 0.5 U
MNW-14 (I2)PCE 0.5 UTCE 38.2 =cis-DCE 7.7 =trans-DCE 1.1 =VC 0.5 U
MNW-8 (I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-9 (I2)PCE 0.5 UTCE 2.8 =cis-DCE 1.3 =trans-DCE 0.5 UVC 0.5 U
SFMW-10 (I2)PCE 0.5 UTCE 20.3 =cis-DCE 2.2 =trans-DCE 0.8 =VC 0.5 U
SFMW-17 (I2)PCE 0.5 UTCE 7.6 =cis-DCE 3.9 =trans-DCE 2.2 =VC 0.5 U
SFMW-21 (I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-26 (I2)PCE 0.5 UTCE 2.2 =cis-DCE 1.2 =trans-DCE 0.5 UVC 0.5 U
SFMW-27 (I2)PCE 0.5 UTCE 13.4 =cis-DCE 4.9 =trans-DCE 2.5 =VC 0.5 U
SFMW-28 (I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-37 (I2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-47 (I1/I2)PCE 0.5 UTCE 20.6 =cis-DCE 5.3 =trans-DCE 0.7 =VC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary10
20
5 I2/D1E-I1
D2E-I3
D2E-P1
011566
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\FA_TCE_D1.MXD FLONDON 5/1/2014 9:48:47 AM
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Spru
ce S
t
Silver Ave
Copper Ave
St
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
Silver Ave
Marquette Pl
Oak
St
Map
l
Spru
ce S
t
Hig
h S
t
Gold A
Tijeras Ave
Luna
Bl v
d
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
Syca
mor
e S
t
7th
St
Ced
ar S
t
Edith
Blvd
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7th
St
Tijeras Ave
Iron Ave
3rd
St
4th
St
Arno
St
11th
St
Fruit Ave Lomas Blvd
5th
St
Lead Ave
10th
St
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
SH 4
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
MNW-11 (D1)PCE 0.5 UTCE 23.4 =cis-DCE 10.2 =trans-DCE 11.8 =VC 0.5 U
MNW-12 (D1)PCE 0.5 UTCE 0.7 =cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-13 (D1)PCE 0.5 UTCE 1.2 =cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-14 (D1)PCE 0.5 UTCE 0.8 =cis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-4 (D1)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-5 (D1)PCE 1.2 =TCE 8.9 =cis-DCE 5.6 =trans-DCE 2.2 =VC 0.5 U
MNW-9 (D1)PCE 0.5 UTCE 3.1 =cis-DCE 1 =trans-DCE 0.6 =VC 0.5 U
SFMW-14 (D1)PCE 0.5 UTCE 14.8 =cis-DCE 0.8 =trans-DCE 0.5 UVC 0.5 U
SFMW-22 (D1)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-38 (D1)PCE 0.5 UTCE 2.4 =cis-DCE 2.7 =trans-DCE 1 =VC 0.5 U
SFMW-46 (D1/D2)PCE 0.5 UTCE 0.8 =cis-DCE 1 =trans-DCE 0.5 UVC 0.5 U
MNW-16 (D1)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
105
5
I2/D1E-I1
D2E-I3
D2E-P1
011567
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\FA_TCE_D2.MXD FLONDON 6/6/2014 6:05:30 AM
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Spru
ce S
t
Silver Ave
t
Copper Ave
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
Silver Ave
Marquette Pl
Oak
St
Map
le S
t
Spru
ce S
t
Hig
h S
t
Gold Ave
Tijeras Ave
Luna
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
Syca
mor
e S
t
Sp
7th
St
Ced
ar S
t
Edith
Blvd
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7th
St
Tijeras Ave
Iron Ave
3rd
St
4th
St
Arno
St
11th
St
Fruit Ave
Coal Ave
Lomas Blvd
5th
St
Lead Ave
10th
St
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
SH 4
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
McDonald’s (D2)PCE 0.5 UTCE 6.6 =cis-DCE 2.1 =trans-DCE 1.2 =VC 0.5 U MNW-13 (D2)
PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-4 (D2)PCE 0.5 UTCE 2.6 =cis-DCE 2.8 =trans-DCE 0.6 =VC 0.5 U
MNW-5 (D2)PCE 0.8 =TCE 15.4 =cis-DCE 9.5 =trans-DCE 4.2 =VC 0.5 U
SFMW-23 (D2)PCE 0.5 UTCE 4 =cis-DCE 1.6 =trans-DCE 0.5 UVC 0.5 U
SFMW-39 (D2)PCE 0.5 UTCE 0.6 =cis-DCE 1.9 =trans-DCE 0.7 =VC 0.5 U
SFMW-44 (D2)PCE 0.8 =TCE 13.2 =cis-DCE 7.4 =trans-DCE 3 =VC 0.5 =
SFMW-46 (D1/D2)PCE 0.5 UTCE 0.8 =cis-DCE 1 =trans-DCE 0.5 UVC 0.5 U
D2E-P1 (D2)PCE 0.5 UTCE 2.5 =cis-DCE 1.0 =trans-DCE 0.5 UVC 0.5 U
MNW-16 (D2)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
10
5
I2/D1E-I1
D2E-I3
D2E-P1
011568
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\FA_TCE_D3.MXD FLONDON 5/1/2014 10:01:42 AM
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Spru
ce S
t
Silver Ave
Copper Ave
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
Silver Ave
Marquette Pl
Oak
St
Sycam
ore S
Map
le S
t
Spru
ce S
t
Hig
h S
t
Gold Ave
g Rd
Tijeras Ave
Luna
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
Syca
mor
e S
t
Spruce St
7th
St
Ced
ar S
t
Edith
Blvd
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7th
St
ras Ave
Iron Ave
3rd
St
4th
St
Arno
St
11th
St
Fruit Ave
Coal Ave
Lomas Blvd
5th
St
Lead Ave
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
SH 4
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
MNW-13 (D3)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-4 (D3)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-5 (D3)PCE 0.5 UTCE 16.1 =cis-DCE 9 =trans-DCE 4.8 =VC 0.5 U
MNW-6 (D3)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-35 (D3)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-40 (D3)PCE 0.5 UTCE 8.5 =cis-DCE 4.4 =trans-DCE 0.7 =VC 0.5 U
SFMW-41 (D3/D4)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
MNW-16 (D3)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
10
5
I2/D1E-I1
D2E-I3
D2E-P1
011569
R:\FRUITAVENUE_345406\MAPFILES\FEB_2014\FA_TCE_D4.MXD FLONDON 5/1/2014 10:04:09 AM
Fruit Avenue Plume Superfund SiteAlbuquerque, NM
Spru
ce S
t
Silver Ave
Copper Ave
Tijeras Ave
Don
Cip
riano
Ct
Slate Ave
Silver Ave
Marquette Pl
Oak
St
Sycam
or
Map
le S
t
Spru
ce S
t
Hig
h S
t
Gold Ave
Tijeras Ave
Luna
Blv
d
1st S
t
Elm
St
5th
St
Gold Ave
6th
St
Medical Arts Ave
Ridge P
l
Slate Ave
Page Ave
Park Ave
Marble Ave
Tijeras Ave
Silver Ave
Kent Ave
Kele
her A
ve
Syca
mor
e S
t
Spruce St
7th
St
Ced
ar S
t
Edith
Blvd
Copper Ave
9th
St
Marquette Ave
Tijeras Ave
8th
St
9th
St
2nd
St
Roma Ave
Gold Ave
Enci
no P
l
7th
St
eras Ave
Iron Ave
3rd
St
4th
St
Arno
St
11th
St
Fruit Ave
Coal Ave
Lomas Blvd
5th
St
Lead Ave
Silver Ave
Mul
berr
y S
t
Slate Ave
Marquette Ave
Edith
Blv
d
Central Ave
Dr Martin Luther King Jr Ave
Tran
quili
no C
t
Marble Ave
Inte
rsta
te 2
5
6th
St
Lomas Blvd
Coal Ave
Lead Ave
SH 4
7
SH 4
7
La Posada Hotel
WellsFargo
Galleria
IceHouse
First StateBank
PlazaDel Sol
AmericanLinen
Springer PlazaOffice Complex
Plaza
ParkingLotCity
NationsBank
CourtHouse
DetentionCenter
PoliceStation
City/CountyBuilding
CompassBank
MNW-5 (D4)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
SFMW-41 (D3/D4)PCE 0.5 UTCE 0.5 Ucis-DCE 0.5 Utrans-DCE 0.5 UVC 0.5 U
Fruit Avenue Plume Site,Groundwater Use Restriction Boundary
I2/D1E-I1
D2E-I3
D2E-P1
011570
ES050514041759SPB
FIGURE 16 Trichloroethene Concentra ons by Passive Diffusion Bag in Monitoring Well McDonalds (D2)Fruit Avenue Plume Superfund Site, Albuquerque, NM
0
1
2
3
4
5
6
7
8
90 2 4 6 8 10 12
PDB
(fee
tbel
owto
pof
scre
en)
Trichloroethene Concentration (micrograms per liter, μg/L)
McDonalds (D2)
Feb 11
Aug 11
Feb 12
Aug 12
Feb 13
Aug 13
Feb 14
Recommend sampling the 8 foot PDB as it hasconsistently shown the highest TCE concentration
011571
ES050514041759SPB
FIGURE 17 Trichloroethene Concentra ons by Passive Diffusion Bag in Monitoring Well SFMW-28(I2)Fruit Avenue Plume Superfund Site, Albuquerque, NM
0
1
2
3
4
5
6
7
8
90 2 4 6 8 10 12
PDB
(fee
tbel
owto
pof
scre
en)
Trichloroethene Concentration (micrograms per liter, μg/L)
SFMW 28(I2)
Oct 09
Sep 10
Feb 11
Aug 11
Aug 12
Feb 13
Aug 13
Feb 14
Recommend sampling the 5 foot PDB because it is set in centerof screen interval and has shown 1 of the 2 TCE detections
Note: 22 of 24 analytical results arenondetect, represented in this figureas 0.25 μg/L.
011572
This page intentionally left blank.
011573
Appendix B CLP Traffic Reports
011574
APPENDIX B: CLP TRAFFIC REPORTS
This page intentionally left blank.
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX B ES110514201639SPB
011575
Page 1 of3
USEPA CLP Organics COC (LAB COPY)
DateSh1pped: 8/25/2014
CarrierName: UPS
AirbillNo: 1 Z703AY90191456554
Sample lde.ntifier CLP Matrix/Sampler Sample No.
EB01-0814 I Blank/ Todd
I Arrowood
j McDonalds-02-2- I GW/ Todd 0814 Arrowood
McDonalds-02-5- I GW/ Todd 0814 Arrowood
McDonalds-02-8- GW/Todd 0814 Arrowood
MNW-4-02-7- GW/Todd 0814 Arrowood
MNW-5-01-12- GW/ Todd 0814 Arrowood
MNW-5-01-7- GW/ Todd 0814 Arrowood
MNW-5-02-r- I GW/ Todd 0814 Arrowood
MNW-5-03-17- GW/Todd 0814 I Arrowood
Coll.
I Method I Grab
I Grab
Grab
I
Grab
Grab
Grab
I Grab I
Grab
Grab
CHAIN OF CUSTODY RECORD
Case#:
Cooler#; CH2M1
Analysis/Turnaround I Tag/PreservatiVE!/Bottles (Days) '
VOA(35) I 6428300 (HCI), 642•B301 (HCI). 6428302 (HCt) (3) I
location
EB01-0814 :
No: 6-082114-142338-0006 Lab: USEPA Region 6 Lab
Lab Contact; Christy Warren
Lab Phone; 218-983-2137
Collection For Lab Use Date/Time Only
I 081251201412:55 I
VOA(35) 6428310 (HCI). 642.8311 (HCI), I McDonalds-02- I 08/2512014 08:28 6428312 (HCI) (3) 2-0814
VOA(35) 6428313 (HCI), 6428314 (HCI), McOonalds-02- 08/25/2014 08:25 6428315 (HCI), 6428316 (HCI), 5-0814 6428317 (HCI), 642.8318 (HCI), 6428319 (HCI), 642.8320 (HCI),
6428321 (HCI) (9)
VOA(35) 6428322 (HCI), 642·8323 (HCI), McDonalds-02- 08/25/2014 08:20 6428324 (HCI) (3) 8-0814
VOA(35) 6428343 (HCI), 642°8344 (HCI). MNW-4-02-7- 08/25/2014 11 :05 6428345 (HCl) (3) 0814
VOA(35) 6428346 (HCI). 6428347 (HCI), MNW-5-01-12- 08/25/2014 09:19 6428348 (HCI) (3) 0814
VOA(35) 6428349 (HCI), 6428350 (HCI). MNW-5-01-7- 08/25/2014 09:15 6428351 (HCI) (3) 0814
VOA(35) 6428352 (HCI), 6428353 (HCI), MNW-5-02-7- 08/25/2014 09:55 6428354 (HGI) (3) 0814
VOA(35) 6428355 (HCI), 6428356 (HCI), MNW-5-03-17- 08/25/2014 09:28 6428357 (HC.I) (3) 0814
Sample(s) to be used for Lab QC: McOonalds-02-5-0814 Tag 6428313. McOonalds-02-5-0814 Tag 6428314. McOonalds-02-5- I Shipment for Case Complete? Y
10814 Tag 6428315, McDonalds-02-5-0814 Tag 6428316. McDonalds-02-5-0814 Tag 6428317. McOonalds-02-5-0814 Tag 6428318, McOonalds-02-5-0814 Tag 6428319, McOonalds-02-5-0814 Tag 6428320. McOonalds-02-5-0814 Tag 6428321
Analysis Key: VOA:: Trace VOA
Samples Transferred From Chain of Custody#
I
I
Items/Reason Relinquished by (Signature and Organization) I Date/Time Received by (Signature and Organization) Date/Time Sample Condition Upon Receipt I :'.::> - ---.... 1,;2 f/lt( ltuo I
I
-I
T., 1J.Atr1 "'•91 I I
I I I : I
I I I ! I l
011576
Page 2 of 3
I
!
I
USEPA CLP Organics COC (LAB COPY)
OateShipped: 8/25/2014
CarrierName: UPS
Airbil lNo: 1Z703AY90191456554
Sample Identifier , CLP Matrix/Sampler I Sample No.
MNW-5-03-17- GW/ Todd 0814-FD Arrowood I
SFMW-20-11 -5- GW/ Todd 0814 Arrowood
SFMW-21-12-12- GW/ Todd 0814 Arrowood
SFMW-21-12-1 7- I GW/ Todd 0814 Arrowood
SFMW-22-01-8- GW/Todd 0814 Arrowood
I I
I I SFMW-23-02-5- GW/ Todd
0814 Arrowood I SFMW-35-03-5- I GW/Todd I
0814 Arrowood I SFMW-41-03/04- GW/ Todd
5-0814 Arrowood
SFMW-44-02-12-
I GW/ Todd
081 4 Arrowood
Coll. Method
Grab
Grab
Grab
Grab
Grab
I Grab
I
Grab I
Grab
Grab
CHAIN OF CUSTODY RECORD
Case#:
Cooler#: CH2M1
Analysis/Turnaround Tag/PreservativE1/Bottles Location (Days)
VOA(35) 6428358 (HCI). 64213359 (HCI). MNW-5-03-17-6428360 (HCI) (3) 0814-FD
VOA(35) 6428382 (HCI), 6428383 (HCI). SFMW-20-11-5-6428384 (HCI) (3) 0814
VOA(35) 6428385 (HCI), 6428386 (HCI), SFMW-21-12-12-6428387 (HCI (3) 0814
VOA(35) 6428388 (HCI), 64213389 (HCI), ! SFMW-21-12-17-6428390 (HCI) (3) , 0814
No: 6-082114-142338-0006 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection I For Lab Use Date/Time I Only
0812512014 09:30 I
0812512014 12:25 I 08/25/2014 12:08
08125/2014 12:12
VOA(35) 6428391 (HCI), 64213392 (HCI), SFMW-22-01-8- 1 08/25/2014 12:38 6428393 (HCI), 6428394 (HCI), 0814 6428395 (HCI), 642:3396 (HCI), 6428397 (HCI), 642lg398 (HCI).
6428399 (HCI) (9)
VOA(35) 6428400 (HCI), 6428401 (HCI). SFMW-23-02-5- 08/25/2014 12:30 6428402 (HCI) (3) 0814
VOA(35) I 6428415 (HCI). 6428416 (HCI), SFMW-35-03-5- 08/25/2014 12:00 6428417 (HCI) (3) 0814
VOA(35) 6428418 (HCI). 6428419 (HCI), SFMW-41 - 08/25/2014 11:20 6428420 (HCI) (3) 03/04-5-0814
VOA(35) I 6428421 (HCI). 642:!3422 (HCI), SFMW-44-02- 08/25/2014 08:55 6428423 (HCI) (3) 12-0814
I Sample(s) to be used for Lab QC: SFMW-22-01-8-081 4 Tag 6428391 , SFMW-22-01-8-0814 Tag 6428392. SFMW-22-D1-8-0814 Shipment for Case Complete? Y Tag 6428393. SFMW-22-01-8-0814 Tag 6428394. SFMW-22-01 -8-0814 Tag 6428395, SFMW-22-01 -8-0814 Tag 6428396, Samples Transferred From Chain of Custody # SFMW-22-01-8-0814 Tag 6428397, SFMW-22-01-8-081 4 Tag 6428398, SFMW-22-01-8-0814 Tag 6428399
I Analysis Key: VOA= Trace VOA
Items/Reason Relinquished by (Signature and Organization) Date/Time Received by (Signature and Organization) Datemme Sample Condition Upon Receipt
I : I I I I
I I
I
I
011577
Page 3 of 3
USEPA CLP Organics COC (LAB COPY)
DateShipped: 8/25/2014
CarrierName: UPS
AirbillNo: 1 Z703AY90191456554
Sample Identifier CLP Matrix/Sampler Sample No.
SFMW-44-0 2-17-I
GW/ Todd 0814 Arrowood
SFMW-46-D1 /D2- 1 GW/ Todd 2-0814 Arrowood
TB02-0814 I GW/ Todd Arrowood
I I
I
I I
I
I Special Instructions:
Analysis Key: VOA= Trace VOA
Coll. Method
I Grab
Grab
Grab
I
Items/Reason Relinquished by (Signature and Organization)
I ~ ===>
-r.JJ A111 ,,,,.,.,J_
I I
I l I
I I
CHAIN OF CUSTODY RECORD
Case#:
Cooler#: CH2M1
Analysis/Turnaround T ag/Preservative!/Bottles (Days)
VOA(35) 6428424 (HCI), 64213425 (HCI). 6428426 (HCI (3)
VOA(35) 6428427 (HCI, 64213428 (HCl), 6428429 (HCI) (3)
VOA(35 6428439 (HCI). 6428440 (HCI), 6428441 (HCI) (3)
•
I
I
I Date/Time
' Received by (Signature and Organization)
I rtz.mv ,,J I I I I I
I
I Location
SFMW-44-0 2-17-0814
SFMW-46-01/02-2-0814
TB02-0814
I
I I
No: 6-082114-142338-0006 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection For Lab Use Date/Time Only
08/25/2014 08:50
08/25/2014 10:48
08/25/2014 08:00
I
I
Shipment for Case Complete? Y
Samples Transferred From Chain of Custody#
I Date/Time Sample Condition Upon Receipt
I !
I I
I I
I ~
I I
I
011578
Page 1 of 3
USEPA CLP Organics COC (REGION COPY)
DateShipped: 8/25/2014
CarrierName: UPS
AirbillNo: 1Z703AY90191456554
Sample Identifier CLP I Matrix/Sampler I Sample No. I I
E801-0814 Blank/Todd I
I Arrowood
McOonalds-02-2- j GW/ Todd 0814 l Arrowood
McDonalds-02-5- GW/ Todd 0814 Arrowood
I McDonalds-02-8- GW/Todd
0814 Arrowood
MNW-4-02-7- GW/Todd 0814 Arrowood
MNW-5-01-12-I
GW/ Todd 0814 Arrowood
MNW-5-01-7- GW/ Todd I 0814 Arrowood
MNW-5-02-7- I GW/ Todd 0814 I Arrowood
MNW-5-03-17- GW/ Todd 0814 Arrowood
Coll. Method
Grab
Grab
Grab
Grab
Grab
Grab
Grab I
Grab
Grab I I
CHAIN OF CUSTODY RECORD
Fruit Avenue Plume
Case#:
Cooler#: CH2M1
Analysis/Turnaround I Tag/Preservative!/Bottles (Days)
VOA(35) 6428300 (HCI, 642H301 (HCI). 6428302 (HCll) (3)
VOA(35) 6428310 (HCI), 6428311 (HCI), 6428312 (HCi ) (3)
VOA(35) 6428313 (HCI). 6428314 (HCI). 6428315 (HCI). 64213316 (HCI). 6428317 (HCI), 64213318 (HCJ). 6428319 (HCI), 64213320 (HCI),
I 6428321 (HCll) (9)
VOA(35) I 6428322 (HCI), 64213323 (HCJ). 6428324 (HCll) (3)
VOA(35) 6428343 (HCI, 64213344 (HCI), 6428345 (HCI) (3)
VOA(35) 6428346 (HCI), 64213347 (HCI), 6428348 (HCJ) (3)
VOA(35) I 6428349 (HCI). 6428350 (HCI), 6428351 (HCI) (3)
VOA(35) 6428352 (HCI), 64213353 (HCI), 6428354 (HCI) (3)
VOA(35) 6428355 (HCI), 64213356 (HCI), 6428357 (HCI (3)
1 Sample(s) to be used for Lab QC: McDonalds-02-5-0814 Tag 6428313, McDonalds-02-5-0814 Tag 6428314. McOonalds-02-5-10814 Tag 6428315. McDonalds-02-5-081 4 Tag 6428316, McOonalds-02-5-0814 Tag 6428317, McOonalds-02-5-0814 Tag
6428318. McOonalds-02-5-0814 Tag 6428319, McDonalds-02-5-0814 Tag 6428320. McDonalds-02-5-0814 Tag 64283:21
Analysis Key: VOA=Trace VOA
' Items/Reason Relinquished by (Signature and Organization) I Date/Time Received by (Signature and Organization)
I
~ =:::-.,. ('li'"' 11001 -
T.J~ "''•"'•J I I
I I I
I I I I I I
Location
EB01-0814
No: 6-082114-142338-0006 Lab: USEPA Region 6 Lab
Lab Contact Christy Warren
Lab Phone: 218-983-2137
Collection Sample Type Date/Time
08/25/2014 12:55 Field Sample
McDonalds-02- I 08/25/2014 08:28 Field Sample 2-0814
McDonalds-02- 08/2512014 08:25 Lab QC 5-0814
McDonalds-02- 08/25/2014 08:20 Field Sample 8-0814
MNW-4-02-7- 08/25/2014 11 ;05 Field Sample 0814
MNW-5-01-12- 08/25/2014 09:19 Field Sample 0814 I
MNW-5-01-7- 08/25/2014 09:15 Field Sample 0814 I
MNW-5-02-7- 08/25/2014 09:55 Field Sample 0814
MNW-5-03-17- 08/25/2014 09:28 Field Sample 0814
Shipment for Case Complete? Y
Samples Transferred From Chain of Custody#
Date/Time I Sample Condition Upon Receipt
I
I
'
011579
I I
I
Page 2 of 3
USEPA CLP Organics COC (REGION COPY)
OateSh1pped: 8/25/2014
CarnerName: UPS
AlrbillNo: 1Z703AY90191456554
Sample Identifier I CLP Matrix/Sampler Sample No.
MNW-5-03-17-
I GW/ Todd
0814-FO Arrowood
SFMW-20-11-5- GW/ Todd 0814
' Arrowood
SFMW-21-12-12- GW/ Todd 0814 Arrowood
SFMW-21-12-17- GW/ Todd 0814 Arrowood
SFMW-22-01 -8- I GW/Todd 0814 Arrowood
SFMW-23-02-5- GW/ Todd 0814 I Arrowood
SFMW-35-03-5- I GW/ Todd 0814 Arrowood
SFMW-41-03/04-- GW/Todd 5-0814 Arrowood
SFMW-44-02-12- GW!Todd 0814 Arrowood
Coll. Method
Grab
I
Grab
Grab
Grab
Grab
I
I Grab
Grab I
Grab
Grab
CHAIN OF CUSTODY RECORD
Fruit Avenue Plume
Case#:
Cooler#: CH2M1
Analysis/Turnaround Tag/Preservative!/Bottles (Days)
VOA(35) 6428358 (HCI), 6420359 (HCI), I 6428360 (HCll) (3)
Location
MNW-5-03-17-0814--FO
VOA(35) 6428382 (HCI), 642B383 (HCI), : SFMW-20-11 -5-6428384 (HCl) (3) 0814
VOA(35) 6428385 (HCI). 64213386 (HCI). I SFMW-21-12-12-6428387 (HCil) (3) 0814
No: 6-082114-142338-0006 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection Sample Type Date/Time
08/25/2014 09:30 Field Duplicate
08/25/2014 12:25 Field Sample
08/25/2014 12:08 Field Sample
VOA(35 6428388 (HCI). 642B389 (HCI), SFMW-21-12-17- 108/25/2014 12:12 Fleld Sample 6428390 (HCll) (3) 0814
VOA(35) , 6428391 (HCI), 642!3392 (HCI), SFMW-22-01 -8- 08/25/2014 12:38 Laboe 6428393 (HCI), 64213394 (HCI), 0814 6428395 (HCI), 64213396 (HCI), 6428397 (HCI), 64213398 (HCI),
6428399 (HCI) (9)
VOA35) 6428400 (HCI), 642B401 (HCI). SFMW-23-02-5- 08/25/2014 12:30 Ffeld Sample 6428402 (HCI) (3) 0814
VOA(35) 6428415 (HCI), 6428416 (HCI), SFMW-35-03·5- 08/25/2014 12:00 Field Sample 6428417 (HCI (3) 0814
VOA(35) 6428418 (HCI). 64213419 (HCI). SFMW-41 - I 08/25/201411 :20 Field Sample 6428420 (HCI) (3) 03/04--5-0814 I
VOA(35) 6428421 (HCI). 642B422 (HCI), I SFMW-44--0 2· I 08/2512014 08:55 Field Sample 6428423 (HCI) (3) I 12-0814
I Sample(s) to be used for Lab QC: SFMW-22-01 -8-0814 Tag 6428391 , SFMW-22-01-8-0814 Tag 6428392, SFMW-22-01-8-0814 Shipment for Case Complete? Y Tag 6428393, SFMW-22·01 ·8-0814 Tag 6428394, SFMW-22-01-8-0814 Tag 6428395, SFMW-22-01 -8-0814 Tag 6428396, Samples Transferred From Chain of Custody#
j SFMW-22-01-8-0814 Tag 6428397, SFMW-22-01-8-0814 Tag 6428398. SFMW-22-0 1-8-0814 Tag 6428399
1 Analysis Key: VOA=Trace VOA
I
I
Items/Reason I Relinquished by (Signature and Organization) Oatem me Received by (Signature and Organization) Date/Time I Sample Condition Upon Receipt '
I I TeJrl A_,,~.J I irtt., ff•O
I I I I I I I I
t/l I I
I I I
I I I 1 I . I I I I
I I
011580
Page 3 of 3
USEPA CLP Organics CCC (REGION COPY)
DateShipped: 8/2512014
CarrierName: UPS
AirbillNo: 1 Z703A Y90191456554
Sample Identifier CLP I Matrix/Sampler Sample No.
SFMW-44-02-17- GWITodd 0814 Arrowood
SFMW-46-01/02- GW/ Todd 2-0814 Arrowood
TB02-0814 GWI Todd
l Arrowood
I
I -
I I I
I
I Special Instructions:
I Analysis Key: VOA=Trace VOA
Coll. Method
I Grab
Grab
I
I Grab I
I
I
I
I
CHAIN OF CUSTODY RECORD
Fruit Avenue Plume
Case#:
Cooler#: CH2M1
Analysis!Turnaround Tag/Preservative/Bottles (Days)
VOA(35) 6428424 (HCI). 6428425 (HCI). 6428426 (HCI) (3)
VOA(35) 6428427 (HCI). 64W428 (HCI), 6428429 (HCI) (3)
VOA(35) 6428439 (HCI), 6428440 (HCI), 6428441 (HCI) (3)
.
I
I ltemslReason Relinquished by (Signature and Organization) 1 Date!Time I Received by (Signature and Organization)
l I _.>
I '/11$1,., ,,,.; *T""' t,,..,,,... ~ I
I I
I I
I I I I I I I I
I Location
I SFMW-44-02-
17-0814
SFMW-46-01 /02-2-0814
TB02-0814
l
I
No: 6-082114-142338-0006 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection Sample Type Date!Time
08/25/2014 08:50 Field Sample
08/251201 4 10:48 Field Sample ! I 08/25/2014 08:00 Blank
I I
l I I
I I
I
Shipment for Case Complete? Y
Samples Transferred From Chain of Custody#
Oate!Time Sample Condition Upon Receipt I
I
I
I I l
011581
Page 1of3
USEPA CLP Organics COC (REGION COPY)
DateSh ipped: 8/25/2014
CarrierName: UPS
AirblllNo: 1 Z703AY90190587976
Sample Identifier CLP Matrix/Sampler Sample No.
HSM-12-5-17-0814 1 GW/ Todd Arrowood
HSM-12-5-17- GW/Todd 0814-FO Arrowood
MNW-11-01-2- GW/Todd 082014 Arrowood
MNW-1 4-01-7- GW/Todd 0814 Arrowood
MNW-14-12-2- GW/Todd 0814 Arrowood
MNW-1 4-12-2- GW/Todd 0814-FO Arrowood
MNW-1 4-12-8· GW/Todd 0814 Arrowood
MNW-1-12-7-0814 GW/Todd Arrowood
MNW-8-12-7-0814 GW/Todd Arrowood
MNW-9-01 -2- GW/ Todd 0814 Arrowood
Special Instructions:
I Analysis Key: VOA= Trace VOA
Coll. Method
Grab
Grab
Grab
Grab
Grab
Grab
Grab I
Grab I
Grab
Grab
Items/Reason Relinquished by (Signature and Organization)
~ ...,
l
Tbtl J Ar1.,_o' I
I
I
CHAIN OF CUSTODY RECORD
Fruit Avenue Plume
Case#:
Cooler#: NMED1
Analysis/Turnaround Tag/Preservative/Bottles (Days)
VOA(35) 6428304 (HCI), 6428305 (HCI). 6428306 (HCI) (3)
VOA35) 6428307 (HCI). 6428308 (HCI). 6428309 (HC:I) (3)
VOA35) 6428325 (HCI), 6428326 (HCI), 6428327 (HC:I) (3)
VOA35) 6428328 (HCI), 6428329 (HCQ, 6428330 (HCI) (3)
VOA(35) 6428331 (HCI), 6428332 (HCI), 6428445 (HCI) (3)
VOA(35) 6428334 (HCI). 6428335 (HCI), 6642836 HCI) (3)
VOA(35) 6428337 (HCI), 6428338 (HCI), 6428339 (HCI) (3)
VOA(35) 6428340 (HCI), 6428341 (HCI), 6428342 (HCI) (3)
VOA(35) 6428361 (HCI), 6428362 (HCI), I 6428363 (HCI) (3)
VOA(35) 6428364 (HCI). 6428365 (HCI), : 6428366 (HCI) (3) 1
Location
HSM-12-5-17-0814
HSM-12-5-17-0814-FD
MNW-1 1-01-2-082014
MNW-14-01-7-0814
MNW-14-12-2-0814
MNW-14-12-2-0814-FD
MNW-14-12-8-0814
MNW-1-12-7-0814
MNW-8-12-7-0814
MNW-9-01-2-0814
No: 6-082114-134553-0005 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection Sample Type Date/Time
08/25/2014 08:57 Field Sample
08/25/2014 09:57 Field Duplicate
08/25/2014 12:24 Field Sample
08/25/2014 09:56 Field Sample
08/25/2014 09:48 Field Sample
08/25/2014 10:48 Field Duplicate
08/25/2014 09:50 Field Sample
08/25/2014 08:15 Field Sample
08/25/2014 08:04 Field Sample
08/25/2014 12:47 Field Sample
Shipment for Case Complete? Y
Samples Transferred From Chain of Custody #
Date/Time Received by (Signature and Organization) Date/Time Sample Condition Upon Receipt
CflVIY tf .i.
I
011582
Page 2 of 3
USEPA CLP Organics COC (REGION COPY)
DateShipped: 8125/2014
CarrierName: UPS
AirbillNo: 1 Z703A Y90190587976
Sample Identifier CLP Matrix/Sampler Sample No.
MNW-9-01-2- GW/ Todd 0814-FD Arrowood
MNW-9-12-17- GW/Todd 0814 Arrowood
SFMW-14-01-2- GW/Todd 0814 Arrowood
SFMW-17-12-8- GW/Todd 0814 I Arrowood
SFMW-18-11-8- GW/Todd 0814 Arrowood
SFMW-25-11 -5- GW/Todd 0814 Arrowood
SFMW-26-12-2- GW/Todd 0814 Arrowood
SFMW-26-12-8- GW/Todd 0814 Arrowood
SFMW-27-12-8- GW/ Todd 0814 Arrowood
SFMW-47-11/12- GW/ Todd 12-0814 Arrowood
I Special Instructions:
I
I Analysis Key: VOA=Trace VOA
Coll. Method
Grab
Grab
Grab
Grab
Grab
I Grab
I Grab
I Grab
Grab
Grab
I. Items/Reason Relinquished by (Signature and Organization)
I --:::-> - --...,., -
I I
Told Arr-,,..J
I I
I
'
CHAIN OF CUSTODY RECORD
Fruit Avenue Plume
Case#:
Cooler#: NMED1
Analysis/Turnaround Tag/Preservative/Bottles (Days)
VOA(35) 6428367 (HCI), 6428368 (HCI), 6428369 (HCI) (3)
VOA(35) 6428370 (HCI), 6428371 (HCI), 6428372 (HCI) (3)
VOA(35) 6428373 (HCI), 6428374 (HCI), 6428375 (HC:I) (3)
VOA(35) 6428376 (HCI), 6428377 (HCI), I 6428378 (HCI) (3)
VOA(35) 6428379 (HCI), 6428380 (HCI), 6428381 (HC:I) (3)
VOA(35) 6428403 (HCI), 6428404 (HCI), 6428405 (HCI) (3)
VOA(35) 6428406 (HCI), 6428407 (HCI), 6428408 (HC:I) (3)
VOA(35) 6428409 (HCI). 6428410 (HCI). 6428411 (HCI) (3)
VOA(35) 6428412 (HCI), 6428413 (HCI), 6428414 (HCI) (3)
VOA(35) 6428430 (HCI). 6428431 (HCI). 6428432 (HCI) (3)
Location I MNW-9-01 -2-
0814-FO
No: 6-082114-134553-0005 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection Sample Type Date/Time
08/25/2014 13:47 Field Duplicate
MNW-9-12-17 - 08/25/2014 12:37 Field Sample I 0814
SFMW-14-01-2- 08/25/2014 0827 Field Sample 0814
SFMW-17-12-8- 08/25/2014 09: 14 Ffeld Sample 0814 I
SFMW-18-11-8- I 08/25/201410:03 Field Sample 0814
SFMW-25-11-5- 08/25/2014 13: 19 Field Sample 0814
SFMW-26-12-2- 08/25/2014 13:08 Field Sample 0814
SFMW-26-12-8- 08125/2014 13:09 Field Sample 0814
SFMW-27-12-8- 08/25/2014 10: 18 Field Sample 0814
SFMW-47-11/12- 08125/2014 08:44 Field Sample 12-0814 I
I
I Shipment for Case Complete? Y
I Samples Transferred From Chain of Custody#
I
Date/Tfme Received by (Signature and Organization) Date/Tfme Sample Condition Upon Receipt
I
/l/1-$/t'f """ I
I I
- I
011583
Page 3 of 3
USEPA CLP Organics COC (REGION COPY)
DateShipped: 8/25/2014
CarrierName: UPS
AirbillNo: 1 Z703A Y90190587976
Sample Identifier
1
CLP Matrix/Sampler I Sample No. I
SFMW-47-11/12- GW/ Todd
I 22-0814 I Arrowood
TB01-0814 I GW/ Todd I Arrowood
I
I
I I
1
Special Instructions:
I Analysis Key: VOA=Trace VOA
Coll. Method
Grab
Grab
Items/Reason Relinquished by (Signature and Organization)
1--=- - ---' 11 u ft,,.,., Q!!J
1
I
I
I
CHAIN OF CUSTODY RECORD
Fruit Avenue Plume
Case#:
Cooler#: NMED1
Analysis/Turnaround Tag/Preservativ1~/Bottles (Days)
VOA(35) 6428433 (HCI), 6428434 (HCI, 6428435 (HCI) (3)
VOA(35) 6428436 (HCI), 6428437 (HCI), 6428438 (HCI) (3)
Location
SFMW-47-11112-22-0814
TB01-0814
I
I
:
No: 6-082114-134553-0005 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection Sample Type Date/Time I
08/25/2014 08:46 I Field Sample
08/25/2014 08:00 Blank
Shipment for Case Complete? Y
I Samples Transferred From Chain of Custody#
Date/Time Received by (Signature and Organization) Date/Time Sample Condition Upon Receipt I
f(tJ/t'( ,,., tJ
I
I
.
' I
'
011584
Page 1 of 3
USEPA CLP Organics COC (LAB COPY)
DateShipped: 8125/2014
CarrierName: UPS
AirbillNo: 1Z703AY90190587976
Sample Identifier CLP Matrix/Sampler Sample No.
HSM-12-5-17-081 4 GW/Todd Arrowood
HSM-12-5-17- I GW/ Todd 0814-FD Arrowood
MNW-11-D1-2- GW/ Todd 082014 Arrowood
r MNW-14-D1-7- GW/Todd 0814 Arrowood
MNW-14-12-2- GW/ Todd 0814 Arrowood
MNW-14-12-2- GW/Todd 0814-FD Arrowood
MNW-14-12-8- GW/ Todd 0814 Arrowood
MNW-1-12-7-0814 GW/ Todd Arrowood
MNW-8-12-7-0814 GW/Todd Arrowood
MNW-9-D1-2- GW/Todd 0814 Arrowood
Special Instructions:
Analysis Key; VOA=Trace VOA
Coll. Method
Grab
Grab
Grab
Grab
Grab
Grab
Grab
Grab
Grab
Grab I
Items/Reason Relinquished by (Signature and Organization)
' - £ ~
I T ... ' d_/rf_1.,..,,.. / I
I I
I I
I
I
CHAIN OF CUSTODY RECORD
Case#:
Cooler#: NMED1
Analysis/Turnaround Tag/Preservativu/Bottles (Days)
VOA(35) 6428304 (HCI). 642•8305 (HCI), 6428306 (HCI) (3)
VOA(35) 6428307 (HCI), 642.8308 (HCI), 6428309 (HCI) (3)
VOA(35) 6428325 (HCI). 6428326 (HCI), 6428327 (HCI) (3)
VOA(35) 6428328 (HCI). 642:'3329 (HCI). 6428330 (HCI) (3)
VOA(35) 6428331 (HCI). 642•8332 (HCI), 6428445 (HCI) (3)
VOA(35) 6428334 (HCI), 642:8335 (HCI), 6642836 (HCI) (3)
VOA(35) 6428337 (HCI). 642•8338 (HCI), 6428339 (HCI) (3)
VOA(35) 6428340 (HCI), 6428341 (HCI), 6428342 (HCI) (3)
VOA35) 6428361 (HCI), 6428362 (HCI), 6428363 (HCI) (3)
VOA(35) 6428364 (HCI). 642.8365 (HCI), 6428366 (HCI) (3)
Date/Time Received by (Signature and Organization)
!111/l'i rev.
Location
HSM-12-5-17-0814
HSM-12-5-17-081 4-FD
MNW-11-D1-2-082014
MNW-14-D1-7-0814
MNW-1 4-12-2-0814
MNW-1 4-12-2-0814-FD
MNW-1 4-12-8-0814
MNW-1-12-7-0814
MNW-8-12-7-0814
MNW-9-D1-2-081 4
I
No: 6-082114-134553-0005 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection For Lab Use Date/Time Only
08/25/2014 08:57
08/25/2014 09:57
0812512014 12:24 I
08/25/2014 09:56 I
08/25/2014 09:48
08/25/2014 10:48
08/25/2014 09:50
08/25/2014 08:15
08/25/2014 08:04
08/25/2014 12:47
Shipment for Case Complete? Y
Samples Transferred From Chain of Custody#
Date/Time Sample Condition Upon Receipt
I
I
I I
011585
Page 2 of 3
USEPA CLP Organics COC (LAB COPY)
DateShipped: 8/25/2014
CarrierName: UPS
AirbillNo: 1Z703AY90190587976
Sample Identifier CLP Matrix/Sampler Sample No.
MNW-9-D1-2- GW/Todd 0814-FD Arrowood
MNW-9-12-17- I GW/ Todd 0814 Arrowood
I SFMW-14-D1-2- GW/Todd
0814 Arrowood
I SFMW-17-12-8- I GW/ Todd 0814 Arrowood
SFMW-18-11-8- GW/Todd
I 0814 Arrowood
SFMW-25-11-5- GW/ Todd 0814 Arrowood
SFMW-26-12-2- GW/ Todd 0814
' Arrowood
SFMW-26-12-8- I GW/ Todd 0814 I Arrowood
SFMW-27-12-8- GW/ Todd 0814 I I Arrowood
SFMW-47-11112- GW/ Todd
I 12-0814 Arrowood
I Special Instructions:
I Analysis Key: VOA= Trace VOA
CHAIN OF CUSTODY RECORD
Case#:
Cooler#: NMED1
Coll. AnalysisJTumaround Tag/PreservativE1/8ottles Method (Days)
Grab VOA(35) 6428367 (HCI), 64213368 (HCI), 6428369 (HCI) (3)
Grab
I VOA(35) 6428370 (HCI), 6428371 (HCI),
6428372 (HCJ) (3)
Grab VOA(35) ' 6428373 (HCI). 6428374 (HCI). 6428375 (HCI) (3)
Grab VOA(35) 6428376 (HCI), 6428377 (HCI), 6428378 (HCI) (3)
Grab VOA(35) 6428379 (HCI), 64213380 (HCI), 6428381 (HCI) (3)
Grab VOA(35) 6428403 (HCI), 642'3404 (HCI), I 6428405 (HCI) (3)
Grab VOA(35) 6428406 (HCI), 642:6407 (HCI), 6428408 (HC1) (3)
I Grab VOA(35) 6428409 (HCI), 6428410 (HCI). 6428411 (HCI) (3)
Grab VOA(35) I 6428412 (HCI), 6428413 (HCI). 6428414 (HCI) (3)
Grab
I VOA(35) 6428430 (HCI), 642.8431 (HCI),
• 6428432 (HCI) (3)
Items/Reason Relinquished by (Signature and Organization) 1 Date/Time Received by (Signature and Organization)
I ~ ..:>
""''~ f (Pt; I I ToJ J ArthvD t'
I I
I I I I l I
No: 6-082114-134553-0005 lab: USEPA Region 6 lab
lab Contact Christy Warren
lab Phone: 218-983-2137
Location I Collection For Lab Use I Date/Time Only 1
MNW-9-D1-2- 08/25/2014 13:47 0814-FD
MNW-9-12-1 7- I 08/25/2014 12:37 0814
SFMW-14-D1-2- 08/25/2014 08:27 0814
SFMW-17 -12-8- 08/25/2014 09:14 0814
SFMW-18-11-8- 08/25/2014 10:03 0814
SFMW-25-11-5- 08/25/2014 13:19 0814 I
SFMW-26-12-2- 08/25/2014 13:08 0814
SFMW-26-12-8· 08/25/2014 13:09 I 0814
SFMW-27-12-8- 08/2512014 10:18 0814
SFMW-47-11/12- 08/25/2014 08:44 12-0814 I I
Shipment for Case Complete? Y
Samples Transferred From Chain of Custody#
Date/Time j Sample Condition Upon Receipt
I
011586
Page 3 of 3
USEPA CLP Organics COC (LAB COPY)
DateShipped: 812512014
CarrierName: UPS
AirbillNo: 1 Z703AY90190587976
Sample Identifier CLP Matrix/Sampler Sample No.
SFMW-47-11112- GW/Todd 22-0814 Arrowood
TB01-0814 GW/ Todd I Arrowood
I
I I
I I
I
I I I
I Special Instructions:
I Analysis Key: VOA=Trace VOA
CHAIN OF CUSTODY RECORD
Case#:
Cooler#: NMED1
Coll. I AnalysisfTurnaround I TaglPreservativE~/Bottles
Method (Days)
Grab VOA(35) 6428433 (HCI), 642:3434 (HCI), 6428435 (HCI) (3)
Grab VOA(35) 6428436 (HCI), 6428437 (HCI), 6428438 (HCI) (3)
I
I
I Items/Reason Relinquished by (Signature and Organization) I Date/Time I Received by (Signature and Organization)
I I '~ 'f!UA'( ,,or,,! I I
'T"'~ MI
I I I I I
I I
I I ' I I I
Location I SFMW-47-11112-
22-0814
TB01-0814
I
I
No: 6-082114-134553-0005 Lab: USEPA Region 6 Lab
Lab Contact: Christy Warren
Lab Phone: 218-983-2137
Collection For Lab Use Date/Time Only
08/25/201 4 08:46
08/25/2014 08:00
Shipment for Case Complete? Y
Samples Transferred From Chain of Custody#
DatefTime Sample Condition Upon Receipt
I
011587
Appendix C VOC Analytical Data Summary Tables
011588
This page intentionally left blank.
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX C ES110514201639SPB
011589
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: DM‐05‐S DM‐06‐I1/I2 DM‐07‐I1/I2 DM‐07‐I1/I2 DM‐08‐I1/I2 DM‐08‐I1/I2 DM‐09‐S SP‐1 SP‐1 SP‐5SamplingPoint: DM‐05‐S‐8 DM‐06‐I1/I2‐2 DM‐07‐I1/I2‐12 DM‐07‐I1/I2‐27 DM‐08‐I1/I2‐12 DM‐08‐I1/I2‐22 DM‐09‐S‐7 SP‐1 SP‐1 SP‐5
SampleID: DM‐05‐S‐8‐022014 DM‐06‐I1/I2‐2‐022014 DM‐07‐I1/I2‐12‐022014 DM‐07‐I1/I2‐27‐022014 DM‐08‐I1/I2‐12‐022014 DM‐08‐I1/I2‐22‐022014 DM‐09‐S‐7‐022014 FAP_SP‐1‐19022014 FAP_SP‐1‐19022014‐FD FAP_SP‐5‐19022014SDate: 2/18/2014 8:18 2/18/2014 8:06 2/17/2014 13:57 2/17/2014 13:59 2/18/2014 10:00 2/18/2014 10:04 2/18/2014 9:51 2/17/2014 13:20 2/17/2014 13:20 2/17/2014 13:25Matrix: GW GW GW GW GW GW GW GW GW GW
SampleType: N N N N N N N N FD NClass Analyte UnitsVOC 1,1,1‐Trichloroethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,1,2,2‐Tetrachloroethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,1,2‐Trichloroethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,1‐Dichloroethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,1‐Dichloroethene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,2,4‐Trichlorobenzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,2‐Dibromo‐3‐chloropropane µg/L 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0UVOC 1,2‐Dibromoethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,2‐Dichlorobenzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,2‐Dichloroethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,2‐Dichloropropane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,3‐Dichlorobenzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 1,4‐Dichlorobenzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC 2‐Butanone µg/L 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0UVOC 2‐Hexanone µg/L 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0UVOC 4‐Methyl‐2‐pentanone µg/L 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0UVOC Acetone µg/L 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 9.5 5.0U 5.0U 5.0UVOC Benzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Bromodichloromethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Bromoform µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 1.5VOC Bromomethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Carbon disulfide µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Carbon tetrachloride µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Chlorobenzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Chloroethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Chloroform µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 1.6 1.6 1.8VOC Chloromethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC cis‐1,2‐Dichloroethene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.9 1.0 0.5UVOC cis‐1,3‐Dichloropropene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Cyclohexane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Dibromochloromethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.6VOC Dichlorodifluoromethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Ethylbenzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Isopropylbenzene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC meta‐/para‐Xylene µg/L 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0UVOC Methyl acetate µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Methyl tert‐butyl ether µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Methylcyclohexane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Methylene chloride µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC ortho‐Xylene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC pH µg/L 2.0 2.0 2.0 2.0 2.0 2.0 2.0 7.0 7.0 7.0VOC Styrene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Tetrachloroethene µg/L 0.7 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Toluene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC trans‐1,2‐Dichloroethene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC trans‐1,3‐Dichloropropene µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Trichloroethene µg/L 0.5U 0.9 0.5U 0.5U 0.5U 0.5U 0.5U 2.4 2.5 0.5UVOC Trichlorofluoromethane µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UVOC Vinyl chloride µg/L 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5UNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New Mexico
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 1 OF 13
011590
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoHSM‐I2‐5 McDonalds‐D2 McDonalds‐D2 McDonalds‐D2 MNW‐11‐D1 MNW‐12‐D1 MNW‐13‐D1 MNW‐13‐D2 MNW‐13‐D2
HSM‐I2‐5‐17 McDonalds‐D2‐2 McDonalds‐D2‐5 McDonalds‐D2‐8 MNW‐11‐D1‐2 MNW‐12‐D1‐12 MNW‐13‐D1‐7 MNW‐13‐D2‐7 MNW‐13‐D2‐7HSM‐I2‐5‐17‐022014 McDonalds‐D2‐2‐022014 McDonalds‐D2‐5‐022014 McDonalds‐D2‐8‐022014 MNW‐11‐D1‐2‐022014 MNW‐12‐D1‐12‐022014 MNW‐13‐D1‐7‐022014 MNW‐13‐D2‐7‐022014 MNW‐13‐D2‐7‐022014‐FD
2/18/2014 8:50 2/17/2014 8:05 2/17/2014 8:08 2/17/2014 8:10 2/17/2014 12:20 2/17/2014 12:36 2/18/2014 10:55 2/18/2014 10:40 2/18/2014 10:40GW GW GW GW GW GW GW GW GWN N N N N N N N FD
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.8 8.4 9.1 10.2 9.1 7.1 5.0U 6.8 6.6
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.9 0.5U 0.5U 2.1 10.2 0.5U 0.5U 0.5U 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.3 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.8 0.5U 0.5U 1.2 11.8 0.5U 0.5U 0.5U 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U17.9 2.6 2.8 6.6 23.4 0.7 1.2 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 2 OF 13
011591
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoMNW‐13‐D3 MNW‐14‐D1 MNW‐14‐I2 MNW‐14‐I2 MNW‐16‐D1 MNW‐16‐D2 MNW‐16‐D3 MNW‐1‐I2 MNW‐1‐I2 MNW‐4‐D1
MNW‐13‐D3‐7 MNW‐14‐D1‐7 MNW‐14‐I2‐2 MNW‐14‐I2‐8 MNW‐16‐D1‐12 MNW‐16‐D2‐12 MNW‐16‐D3‐12 MNW‐1‐I2‐7 MNW‐1‐I2‐7 MNW‐4‐D1‐12MNW‐13‐D3‐7‐022014 MNW‐14‐D1‐7‐022014 MNW‐14‐I2‐2‐022014 MNW‐14‐I2‐8‐022014 MNW‐16‐D1‐12‐022014 MNW‐16‐D2‐12‐022014 MNW‐16‐D3‐12‐022014 MNW‐1‐I2‐7‐022014 MNW‐1‐I2‐7‐022014‐FD MNW‐4‐D1‐12‐022014
2/18/2014 10:25 2/17/2014 10:55 2/17/2014 10:44 2/17/2014 10:49 2/18/2014 9:15 2/18/2014 8:55 2/18/2014 8:20 2/17/2014 8:20 2/17/2014 9:20 2/18/2014 10:00GW GW GW GW GW GW GW GW GW GWN N N N N N N N FD N
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.6 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U6.8 7.0 8.9 7.8 5.7 5.3 6.3 8.5 9.2 7.3
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 1.2 0.5U 0.5U 0.5U0.5U 0.5U 0.9 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 7.6 7.7 0.5U 0.5U 0.5U 4.1 3.8 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 1.4 0.5U 0.8 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 1.1 1.1 0.5U 0.5U 0.5U 1.0 0.9 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.8 32.4 38.2 0.5U 0.5U 0.5U 19.0 17.8 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 3 OF 13
011592
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoMNW‐4‐D2 MNW‐4‐D3 MNW‐5‐D1 MNW‐5‐D1 MNW‐5‐D2 MNW‐5‐D3 MNW‐5‐D4 MNW‐6‐D3 MNW‐8‐I2 MNW‐9‐D1
MNW‐4‐D2‐7 MNW‐4‐D3‐7 MNW‐5‐D1‐12 MNW‐5‐D1‐7 MNW‐5‐D2‐7 MNW‐5‐D3‐17 MNW‐5‐D4‐7 MNW‐6‐D3‐7 MNW‐8‐I2‐7 MNW‐9‐D1‐2MNW‐4‐D2‐7‐022014 MNW‐4‐D3‐7‐022014 MNW‐5‐D1‐12‐022014 MNW‐5‐D1‐7‐022014 MNW‐5‐D2‐7‐022014 MNW‐5‐D3‐17‐022014 MNW‐5‐D4‐7‐022014 MNW‐6‐D3‐7‐022014 MNW‐8‐I2‐7‐022014 MNW‐9‐D1‐2‐022014
2/18/2014 9:47 2/18/2014 9:40 2/18/2014 12:07 2/18/2014 12:05 2/18/2014 11:48 2/18/2014 11:30 2/18/2014 11:20 2/17/2014 12:20 2/17/2014 8:00 2/17/2014 10:15GW GW GW GW GW GW GW GW GW GWN N N N N N N N N N
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.6 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U10.9 5.0U 7.3 5.0U 6.8 8.2 5.0U 5.0U 5.0U 5.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.8 0.5U 3.6 5.6 9.5 9.0 0.5U 0.5U 0.5U 1.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 1.2 0.8 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.6 0.5U 1.6 2.2 4.2 4.8 0.5U 0.5U 0.5U 0.6
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.6 0.5U 4.4 8.9 15.4 16.1 0.5U 0.5U 0.5U 3.1
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 4 OF 13
011593
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoMNW‐9‐I2 SFMW‐10‐I2 SFMW‐14‐D1 SFMW‐14‐D1 SFMW‐16‐I1 SFMW‐17‐I2 SFMW‐17‐I2 SFMW‐18‐I1 SFMW‐20‐I1
MNW‐9‐I2‐17 SFMW‐10‐I2‐8 SFMW‐14‐D1‐2 SFMW‐14‐D1‐2 SFMW‐16‐I1‐8 SFMW‐17‐I2‐8 SFMW‐17‐I2‐8 SFMW‐18‐I1‐8 SFMW‐20‐I1‐5MNW‐9‐I2‐17‐022014 SFMW‐10‐I2‐8‐022014 SFMW‐14‐D1‐2‐022014 SFMW‐14‐D1‐2‐022014‐FD SFMW‐16‐I1‐8‐022014 SFMW‐17‐I2‐8‐022014 SFMW‐17‐I2‐8‐022014‐FD SFMW‐18‐I1‐8‐022014 SFMW‐20‐I1‐5‐022014
2/17/2014 10:07 2/17/2014 9:08 2/17/2014 9:25 2/17/2014 10:25 2/18/2014 9:33 2/18/2014 9:23 2/18/2014 10:23 2/17/2014 11:05 2/17/2014 8:57GW GW GW GW GW GW GW GW GWN N N FD N N FD N N
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U9.9 7.3 5.8 5.2 5.0U 12.5 15.7 9.1 5.0U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.3 2.2 0.8 0.7 0.8 3.1 3.9 0.9 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 2.1 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.8 0.5U 0.5U 0.5U 1.8 2.2 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.8 20.3 14.8 14.8 5.8 3.7 7.6 1.8 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 5 OF 13
011594
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoSFMW‐21‐I2 SFMW‐21‐I2 SFMW‐22‐D1 SFMW‐22‐D1 SFMW‐23‐D2 SFMW‐25‐I1 SFMW‐26‐I2 SFMW‐26‐I2 SFMW‐27‐I2
SFMW‐21‐I2‐12 SFMW‐21‐I2‐17 SFMW‐22‐D1‐8 SFMW‐22‐D1‐8 SFMW‐23‐D2‐5 SFMW‐25‐I1‐5 SFMW‐26‐I2‐2 SFMW‐26‐I2‐8 SFMW‐27‐I2‐2SFMW‐21‐I2‐12‐022014 SFMW‐21‐I2‐17‐022014 SFMW‐22‐D1‐8‐022014 SFMW‐22‐D1‐8‐022014‐FD SFMW‐23‐D2‐5‐022014 SFMW‐25‐I1‐5‐022014 SFMW‐26‐I2‐2‐022014 SFMW‐26‐I2‐8‐022014 SFMW‐27‐I2‐2‐022014
2/17/2014 9:30 2/17/2014 9:27 2/17/2014 9:10 2/17/2014 9:10 2/17/2014 9:03 2/18/2014 10:18 2/18/2014 10:25 2/18/2014 10:30 2/17/2014 11:17GW GW GW GW GW GW GW GW GWN N N FD N N N N N
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 7.8 5.0U 5.0U 5.0U 9.6 10.2 10.4 8.20.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 1.1 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0 3.6 1.8 1.8 1.4 0.5U 0.5U 0.5U 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 1.6 2.3 0.8 1.2 4.90.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0 0.5U 0.5U 0.5U 1.6 0.5U 0.5U 0.5U 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.9 0.5U 0.5U 2.50.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 4.0 4.6 0.6 2.2 13.40.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 6 OF 13
011595
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoSFMW‐28‐I2 SFMW‐28‐I2 SFMW‐28‐I2 SFMW‐35‐D3 SFMW‐37‐I2 SFMW‐38‐D1 SFMW‐39‐D2 SFMW‐39‐D2 SFMW‐40‐D3
SFMW‐28‐I2‐2 SFMW‐28‐I2‐5 SFMW‐28‐I2‐8 SFMW‐35‐D3‐5 SFMW‐37‐I2‐5 SFMW‐38‐D1‐5 SFMW‐39‐D2‐2 SFMW‐39‐D2‐8 SFMW‐40‐D3‐12SFMW‐28‐I2‐2‐022014 SFMW‐28‐I2‐5‐022014 SFMW‐28‐I2‐8‐022014 SFMW‐35‐D3‐5‐022014 SFMW‐37‐I2‐5‐022014 SFMW‐38‐D1‐5‐022014 SFMW‐39‐D2‐2‐022014 SFMW‐39‐D2‐8‐022014 SFMW‐40‐D3‐12‐022014
2/18/2014 11:05 2/18/2014 11:08 2/18/2014 11:12 2/17/2014 9:38 2/17/2014 8:45 2/18/2014 12:42 2/18/2014 12:23 2/18/2014 12:25 2/18/2014 12:41GW GW GW GW GW GW GW GW GWN N N N N N N N N
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U8.5 5.8 7.3 5.0U 5.0U 5.0U 6.5 6.8 5.9
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 2.4 0.5 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 2.7 2.2 1.9 4.40.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 1.3 0.5U 2.1 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 1.0 0.9 0.7 0.70.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 2.4 0.5U 0.6 8.50.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 7 OF 13
011596
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoSFMW‐41‐D3/D4 SFMW‐44‐D2 SFMW‐44‐D2 SFMW‐46‐D1/D2 SFMW‐46‐D1/D2 SFMW‐47‐I1/I2 SFMW‐47‐I1/I2 SP‐1 SP‐1
SFMW‐41‐D3/D4‐5 SFMW‐44‐D2‐12 SFMW‐44‐D2‐17 SFMW‐46‐D1/D2‐2 SFMW‐46‐D1/D2‐2 SFMW‐47‐I1/I2‐12 SFMW‐47‐I1/I2‐22 SP‐1 SP‐1SFMW‐41‐D3/D4‐5‐022014 SFMW‐44‐D2‐12‐022014 SFMW‐44‐D2‐17‐022014 SFMW‐46‐D1/D2‐2‐022014 SFMW‐46‐D1/D2‐2‐022014‐FD SFMW‐47‐I1/I2‐12‐022014 SFMW‐47‐I1/I2‐22‐022014 FATP_SP‐1‐0814 FATP_SP‐1‐0814‐FD
2/18/2014 12:50 2/17/2014 12:40 2/17/2014 12:53 2/18/2014 12:20 2/18/2014 13:20 2/18/2014 8:37 2/18/2014 8:40 8/27/2014 13:30 8/27/2014 13:40GW GW GW GW GW GW GW GW GWN N N N FD N N N FD
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 2.0U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U14.9 7.1 5.2 9.1 10.8 5.7 5.0U 5.0U 5.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 1.8 1.80.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 7.4 5.7 0.9 1.0 4.9 5.3 1.1 1.20.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 1.9 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 7.0 7.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.8 0.5 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 3.0 2.4 0.5U 0.5U 0.6 0.7 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 13.2 10.4 0.6 0.8 18.5 20.6 3.0 3.00.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 8 OF 13
011597
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoSP‐5 HSM‐I2‐5 HSM‐I2‐5 McDonalds‐D2 McDonalds‐D2 McDonalds‐D2 MNW‐11‐D1 MNW‐14‐D1 MNW‐14‐I2 MNW‐14‐I2SP‐5 HSM‐I2‐5‐17 HSM‐I2‐5‐17 McDonalds‐D2‐2 McDonalds‐D2‐5 McDonalds‐D2‐8 MNW‐11‐D1‐2 MNW‐14‐D1‐7 MNW‐14‐I2‐2 MNW‐14‐I2‐2
FATP_SP‐5‐0814 HSM‐I2‐5‐17‐0814 HSM‐I2‐5‐17‐0814‐FD McDonalds‐D2‐2‐0814 McDonalds‐D2‐5‐0814 McDonalds‐D2‐8‐0814 MNW‐11‐D1‐2‐082014 MNW‐14‐D1‐7‐0814 MNW‐14‐I2‐2‐0814 MNW‐14‐I2‐2‐0814‐FD8/27/2014 14:00 8/25/2014 8:57 8/25/2014 9:57 8/25/2014 8:28 8/25/2014 8:25 8/25/2014 8:20 8/25/2014 12:24 8/25/2014 9:56 8/25/2014 9:48 8/25/2014 10:48
GW GW GW GW GW GW GW GW GW GWN N FD N N N N N N FD
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.7 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 7.7 7.3 16.7 12.2 12.8 12.0 9.7 9.4 8.40.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 6.9 6.4 0.8 0.8 0.9 11.3 0.5U 7.9 7.90.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.7 0.5U 0.5U 0.5U 0.5U 0.5U 1.6 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U4.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 1.1 1.0 0.5U 0.5U 0.5U 12.8 0.5U 1.3 1.20.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 26.0 25.5 6.3 5.0 5.1 29.0 1.6 44.8 44.20.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 9 OF 13
011598
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoMNW‐14‐I2 MNW‐1‐I2 MNW‐4‐D2 MNW‐5‐D1 MNW‐5‐D1 MNW‐5‐D2 MNW‐5‐D3 MNW‐5‐D3 MNW‐8‐I2 MNW‐9‐D1 MNW‐9‐D1
MNW‐14‐I2‐8 MNW‐1‐I2‐7 MNW‐4‐D2‐7 MNW‐5‐D1‐12 MNW‐5‐D1‐7 MNW‐5‐D2‐7 MNW‐5‐D3‐17 MNW‐5‐D3‐17 MNW‐8‐I2‐7 MNW‐9‐D1‐2 MNW‐9‐D1‐2MNW‐14‐I2‐8‐0814 MNW‐1‐I2‐7‐0814 MNW‐4‐D2‐7‐0814 MNW‐5‐D1‐12‐0814 MNW‐5‐D1‐7‐0814 MNW‐5‐D2‐7‐0814 MNW‐5‐D3‐17‐0814 MNW‐5‐D3‐17‐0814‐FD MNW‐8‐I2‐7‐0814 MNW‐9‐D1‐2‐0814 MNW‐9‐D1‐2‐0814‐FD
8/25/2014 9:50 8/25/2014 8:15 8/25/2014 11:05 8/25/2014 9:19 8/25/2014 9:15 8/25/2014 9:55 8/25/2014 9:28 8/25/2014 9:30 8/25/2014 8:04 8/25/2014 12:47 8/25/2014 13:47GW GW GW GW GW GW GW GW GW GW GWN N N N N N N FD N N FD
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.7 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U14.2 15.5 7.6 5.2 6.2 6.0 7.2 7.5 20.2 12.9 20.30.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U8.1 4.3 3.4 3.1 5.6 8.8 9.9 9.8 0.5U 1.3 1.4
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 6.80.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 1.4 0.9 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.1 1.3 0.7 1.3 2.3 3.6 6.1 6.4 0.5U 1.0 1.6
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U39.3 19.7 3.1 3.6 9.7 14.9 16.4 16.2 0.5U 3.6 2.50.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 10 OF 13
011599
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoMNW‐9‐I2 SFMW‐14‐D1 SFMW‐17‐I2 SFMW‐18‐I1 SFMW‐20‐I1 SFMW‐21‐I2 SFMW‐21‐I2 SFMW‐22‐D1 SFMW‐23‐D2 SFMW‐25‐I1 SFMW‐26‐I2
MNW‐9‐I2‐17 SFMW‐14‐D1‐2 SFMW‐17‐I2‐8 SFMW‐18‐I1‐8 SFMW‐20‐I1‐5 SFMW‐21‐I2‐12 SFMW‐21‐I2‐17 SFMW‐22‐D1‐8 SFMW‐23‐D2‐5 SFMW‐25‐I1‐5 SFMW‐26‐I2‐2MNW‐9‐I2‐17‐0814 SFMW‐14‐D1‐2‐0814 SFMW‐17‐I2‐8‐0814 SFMW‐18‐I1‐8‐0814 SFMW‐20‐I1‐5‐0814 SFMW‐21‐I2‐12‐0814 SFMW‐21‐I2‐17‐0814 SFMW‐22‐D1‐8‐0814 SFMW‐23‐D2‐5‐0814 SFMW‐25‐I1‐5‐0814 SFMW‐26‐I2‐2‐0814
8/25/2014 12:37 8/25/2014 8:27 8/25/2014 9:14 8/25/2014 10:03 8/25/2014 12:25 8/25/2014 12:08 8/25/2014 12:12 8/25/2014 12:38 8/25/2014 12:30 8/25/2014 13:19 8/25/2014 13:08GW GW GW GW GW GW GW GW GW GW GWN N N N N N N N N N N
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U10.7 12.8 10.5 13.4 6.6 5.0U 5.0U 5.4 9.1 5.0U 5.30.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 1.3 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.60.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 4.2 2.1 0.5 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.4 1.0 3.8 1.1 0.5U 0.5U 0.5U 0.5U 3.8 3.3 1.1
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.6 3.6 0.5U 0.5U 0.9 0.5U 0.5U 0.5U 0.5U 1.00.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.6 3.2 0.5U 0.5U 0.5U 0.5U 0.5U 0.7 0.7 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.8 18.8 5.6 2.4 0.5U 0.5U 0.5U 0.5U 10.6 7.9 2.5
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 11 OF 13
011600
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoSFMW‐26‐I2 SFMW‐27‐I2 SFMW‐35‐D3 SFMW‐41‐D3/D4 SFMW‐44‐D2 SFMW‐44‐D2 SFMW‐46‐D1/D2 SFMW‐47‐I1/I2 SFMW‐47‐I1/I2 EB‐01
SFMW‐26‐I2‐8 SFMW‐27‐I2‐8 SFMW‐35‐D3‐5 SFMW‐41‐D3/D4‐5 SFMW‐44‐D2‐12 SFMW‐44‐D2‐17 SFMW‐46‐D1/D2‐2 SFMW‐47‐I1/I2‐12 SFMW‐47‐I1/I2‐22 EB‐01SFMW‐26‐I2‐8‐0814 SFMW‐27‐I2‐8‐0814 SFMW‐35‐D3‐5‐0814 SFMW‐41‐D3/D4‐5‐0814 SFMW‐44‐D2‐12‐0814 SFMW‐44‐D2‐17‐0814 SFMW‐46‐D1/D2‐2‐0814 SFMW‐47‐I1/I2‐12‐0814 SFMW‐47‐I1/I2‐22‐0814 EB‐01‐022014
8/25/2014 13:09 8/25/2014 10:18 8/25/2014 12:00 8/25/2014 11:20 8/25/2014 8:55 8/25/2014 8:50 8/25/2014 10:48 8/25/2014 8:44 8/25/2014 8:46 2/18/2014 13:15GW GW GW GW GW GW GW GW GW GWN N N N N N N N N QC
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 2.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 12.5 5.0U 6.6 8.5 12.0 5.5 17.6 16.4 5.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 2.6 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.2 6.1 0.5U 0.5U 7.6 6.8 1.2 5.8 6.2 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 1.0 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0 2.0
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 1.1 0.9 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 4.3 0.5U 0.5U 3.0 2.7 0.5U 1.0 0.9 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.6 14.5 0.5U 0.6 14.3 13.1 1.2 22.6 25.2 0.5U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U
FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 12 OF 13
011601
VOC Analytical Data Summary Tables ‐ Groundwater
StationID: SamplingPoint:
SampleID: SDate: Matrix:
SampleType: Class Analyte UnitsVOC 1,1,1‐Trichloroethane µg/LVOC 1,1,2,2‐Tetrachloroethane µg/LVOC 1,1,2‐Trichloro‐1,2,2‐trifluoroethane µg/LVOC 1,1,2‐Trichloroethane µg/LVOC 1,1‐Dichloroethane µg/LVOC 1,1‐Dichloroethene µg/LVOC 1,2,4‐Trichlorobenzene µg/LVOC 1,2‐Dibromo‐3‐chloropropane µg/LVOC 1,2‐Dibromoethane µg/LVOC 1,2‐Dichlorobenzene µg/LVOC 1,2‐Dichloroethane µg/LVOC 1,2‐Dichloropropane µg/LVOC 1,3‐Dichlorobenzene µg/LVOC 1,4‐Dichlorobenzene µg/LVOC 2‐Butanone µg/LVOC 2‐Hexanone µg/LVOC 4‐Methyl‐2‐pentanone µg/LVOC Acetone µg/LVOC Benzene µg/LVOC Bromodichloromethane µg/LVOC Bromoform µg/LVOC Bromomethane µg/LVOC Carbon disulfide µg/LVOC Carbon tetrachloride µg/LVOC Chlorobenzene µg/LVOC Chloroethane µg/LVOC Chloroform µg/LVOC Chloromethane µg/LVOC cis‐1,2‐Dichloroethene µg/LVOC cis‐1,3‐Dichloropropene µg/LVOC Cyclohexane µg/LVOC Dibromochloromethane µg/LVOC Dichlorodifluoromethane µg/LVOC Ethylbenzene µg/LVOC Isopropylbenzene µg/LVOC meta‐/para‐Xylene µg/LVOC Methyl acetate µg/LVOC Methyl tert‐butyl ether µg/LVOC Methylcyclohexane µg/LVOC Methylene chloride µg/LVOC ortho‐Xylene µg/LVOC pH µg/LVOC Styrene µg/LVOC Tetrachloroethene µg/LVOC Toluene µg/LVOC trans‐1,2‐Dichloroethene µg/LVOC trans‐1,3‐Dichloropropene µg/LVOC Trichloroethene µg/LVOC Trichlorofluoromethane µg/LVOC Vinyl chloride µg/LNotes:µg/L = microgram per literFD = field duplicateN = normal sample. QC = quality control sampleU = The analyte was not detectedGW = groundwater sampleVOC = volatile organic compound
APPENDIX C
Fruit Avenue Plume Superfund Site, Albuquerque, New MexicoTB01 TB02 TB03 TB04 TB07 EB01 TB01 TB02 TB03TB01 TB02 TB03 TB04 TB07 EB01 TB01 TB02 TB03
TB01‐022014 TB02‐022014 TB03‐022014 TB04‐022014 TB07‐022014 EB01‐0814 TB01‐0814 TB02‐0814 TB03‐08142/17/2014 8:15 2/17/2014 8:20 2/18/2014 7:38 2/18/2014 7:40 2/17/2014 13:20 8/25/2014 12:55 8/25/2014 8:00 8/25/2014 8:00 8/27/2014 13:00
GW GW GW GW GW GW GW GW GWQC QC QC QC QC QC QC QC QC
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0U 2.0U 2.0U 2.0U 2.0U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U 5.0U9.3 9.5 13.2 12.4 8.6 32.8 35.6 34.7 5.0U
0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U 1.0U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 20.9 23.5 24.9 0.5U0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U 0.5U2.0 2.0 2.0 2.0 7.0 2.0 2.0 2.0 5.0
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FAP_2014 ANNUAL GW SAMPLING REPORT_APPENDIX CES110514201639SPB PAGE 13 OF 13
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