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Sand Creek Ranch Conservation Community ______________________________________________________________________________ Sand Creek Ranch Conservation Community PUD Potable Water and Waste Treatment Report For Wyoming DEQ By Weston EngineerinG

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  • Sand Creek Ranch Conservation Community

    ______________________________________________________________________________

    Sand Creek Ranch Conservation

    Community

    PUD Potable Water and Waste Treatment Report

    For

    Wyoming DEQ

    By

    Weston EngineerinG

  • Judith MackieNoteThis document contains both letter and Tabloid size pages. To print the whole thing on letter size paper: File - Print - Page Scaling - Reduce to Printer Margins

  • SSAANNDD CCRREEEEKK RRAANNCCHH PPLLAANNNNEEDD UUNNIITT DDEEVVEELLOOPPMMEENNTT

    JOHNSON COUNTY, WYOMING

    RREEPPOORRTT FFOORR MINIMUM STANDARDS FOR

    SUBDIVISION APPLICATIONS DEQ-WQD CHAPTER 23

    FEBRUARY 2007

    PREPARED FOR:

    Sand Creek, the Ranch Preservation Co., LLC

    SUBMITTED TO:

    WYOMING DEPT. OF ENVIRONMENTAL QUALITY WATER QUALITY DIVISION

    PREPARED BY:

    Weston Engineering, Inc.

  • INTRODUCTION This document is prepared for Sand Creek, the Ranch Preservation Co., LLC, to aid in obtaining approval of the Department of Environmental Quality Water Quality Division (DEQ) and the Johnson County Planner for the Sand Creek Ranch Planned Unit Development (PUD) outside Buffalo, Wyoming. This document is formatted to facilitate review of the DEQ following the requirements of DEQ rules and regulations found in Chapters 8, 11, 12, and 23. Figure 1 provides the topography and major geographic features within the development and all areas within one mile of the development boundaries. The base map is adapted from the USGS Lake DeSmet West (1977), Lake DeSmet East (1970), North Ridge (1993), and Buffalo (1970) 1:24,000 topographic quadrangles. Sand Creek Ranch PUD is located in Johnson County in Sections 17, 18, 19, and 20, Township 51 North, Range 82 West and Section 13, Township 51 North, Range 83 West. The proposed development consists of 99 one-acre lots contained within an 850 acre parcel. Approximately 750 acres will be held in common by the homeowners. The Sand Creek Ranch PUD will use individual on-site septic systems and water supply wells because of the low density of the housing units. Covenants and by-laws will allow for installation of wells and adsorption systems on common owned land if needed, on a case-by-case basis. It is possible that at some locations on the PUD that clustered homes may share an adsorption system or water well. This situation will be addressed on a case-by-case basis depending upon the benefits of such systems.

  • SAND CREEK RANCHPUD APPLICATION

    LOCATION MAP FIGURE 1

    N

    WESTON

    SCALE

    SEO PERMITTED WELL LOCATIONS

    HOME SITE LOCATIONS

    SAND CREEK RANCH PUD

    KEY

    T51N

    R 83 W R 82 W

    SPRING COLLECTION POINT

    19272

    50073

    6262819271

    19273

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    2

    CHAPTER 23 - SECTION 7 (a)(i) Type of Sewage System Disposal of domestic sewage will be made with individual on-lot septic systems with adsorption systems. Individual homeowners will be responsible for obtaining permits to install the disposal systems and hiring experienced installers. The Sand Creek Ranch PUD homeowners association will review all building plans prior to construction to ensure that the plans meet the developments restrictive covenants and that they serve not only the good of the individual homeowner, but the community as a whole. At some locations on the PUD up to four homes may share a common adsorption system. At this time it is expected that no more than four homes will share an adsorption system to avoid the requirements of an underground injection control (UIC) permit. (a)(ii-iii) Adequacy of Sewer System Based on the general layout of this development, including the lot size of one acre, lot density, and subsurface conditions, individual on-lot septic disposal is adequate for this development. The Sand Creek Ranch PUD emphasizes residential clusters consisting of between two and 12 homes surrounded by undeveloped natural and agricultural lands. The remainder of this section of the report addresses the details of the sewer system assessment and compliance with applicable rules and regulations. (b)(i-v) New Central Sewage System This section is not applicable to the Sand Creek Ranch PUD because individual on-site septic systems will be used for wastewater disposal. It is anticipated that no more than four- three bedroom homes will be connected to an individual adsorption system to avoid being classified as an UIC facility. (c)(i-iii) Connection to Existing Central Sewage System This section is not applicable to the Sand Creek Ranch PUD because on-site septic systems will be used for wastewater disposal. (d) On-Lot Sewer System (d)(i) Groundwater and Impermeable Soils Separation Soils mapping on the Sand Creek Ranch PUD indicates that there are a total of 14 soil types on the development where houses and/or adsorption systems may be located. Soils mapping was recently completed for the Sand Creek Ranch area by the Buffalo, Wyoming office of the Natural Resources Conservation Service (NRCS). The results of the soils mapping are provided on Figure 2 and descriptions are provided in Table 1. Weston Engineering, Inc. (WESTON) supervised the excavation of a 10-foot deep test pit in each of the soil types. General descriptions of the materials encountered, the thickness of the soils, and the depth to seasonal high groundwater are provided in Table 1. Detailed descriptions of the excavated materials, with photographs, are provided in Appendix A. Four of the fourteen soil types, 67A, 229D, 500, and E33C, have soils less than 10 feet thick. As observed in Table 1, two of the soils have thicknesses of only 7.5 feet. To ensure that the minimum separation of 4 feet from the base of the adsorption system to bedrock is attained as required by DEQ Rules and Regulations Chapter 11, Section 36 (c)(i)., the base must be buried no deeper than 3.5 feet below grade. This condition affects only three home sites in the east-central part of the development.

  • SAN

    D C

    REEK

    RA

    NC

    HPU

    D A

    PPLICA

    TION

    SOILS M

    AP

    FIGU

    RE 2 NWESTO

    N

    SCA

    LE1" = 1,100'

    Percolation Test S

    itesS

    OU

    RC

    E: N

    RC

    S B

    UFFA

    LO FIE

    LD O

    FFICE

  • TAB

    LE 1 SO

    ILS SUM

    MA

    RY TA

    BLE

    SOIL

    TYPE

    SO

    IL NA

    ME

    SO

    IL DESC

    RIPTIO

    N

    SO

    IL TH

    ICK

    NESS

    (feet)

    DEPTH

    TO

    SEASO

    NA

    L HIG

    H

    GR

    OU

    ND

    WA

    TER

    (feet)

    PER

    CO

    LATIO

    N TEST

    RESU

    LTS (m

    inutes per inch) 4A

    Recluse W

    ages Com

    plex

    Pale brow

    n clay loam

    > 11.0

    9.0

    10, 10, 80

    67A

    Moskee Sandy Loam

    Light grayish brown sandy loam

    7.5

    7.5

    8.9, 40, 40

    200DE

    Cragola-Shingle-N

    ihill Com

    plex

    Pale brown gravelly, clay loam

    > 10.0

    > 10.0

    13.3, 16, 20

    229D

    Shingle-Taluce Com

    plex

    Light yellowish sandy loam

    7.5

    7.5

    10, 26.7, 80

    265AB Kishona-Zigw

    eid- Cam

    bria C

    omplex

    Pale brow

    n sandy loam

    > 10.0

    > 10.0

    5.3, 8, 8

    283

    Terro-Orpha-Taluce C

    omplex

    Light brow

    nish gray sandy loam

    > 10.0

    9.0

    40, 20, 40

    367C

    D

    Bowbac-H

    iland Com

    plex

    Yellowish brow

    n sandy clay loam

    > 10.0

    > 10.0

    20, 20, 40

    500

    Haverdad-W

    orthenton Com

    plex

    Pale brown silty loam

    9.5

    > 10.0

    8.9, 10, 16

    508 H

    argreave-Lambm

    an Com

    plex

    Brown sandy loam

    > 10.0

    9.0

    13.3, 13.3, 40

    509 Kishona-Zigw

    eid Com

    plex

    Pale brown sandy loam

    > 10.0

    > 10.0

    40, 40, 40

    E33C

    Hiland Sandy C

    lay Loam

    Yellow

    ish brown sandy clay loam

    8.0

    > 10.0

    20, 26.6, 26.6

    E67D

    Moskee Sandy C

    lay Loam

    Light grayish brow

    n sandy clay loam

    > 10.0

    > 10.0

    8.9, 10, 20

    H

    36 N

    uncho Loam

    D

    ark grayish brown clay loam

    > 10.0

    > 10.0

    26, 26, 40

    X48 H

    eldt Clay Loam

    Brow

    nish gray silty clay

    > 10.0

    4.5

    No Testing

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    3

    Soils excavated from the test pits were examined for evidence of the presence of groundwater. Evidence for shallow groundwater includes wet soils, iron staining, and mottling of materials. As found in Appendix A, minor iron staining was observed at shallow depths in soil types 229D, 500, 508, 509, and E67D. However, with the exception of soil type 229D, these soils have been subjected to flood irrigation for decades and the iron staining is not believed to be from naturally occurring shallow groundwater. Due to drought conditions limiting irrigation water supplies, these soils have not been irrigated for over three years and no evidence of moisture was observed in the test pits. Without flood irrigation occurring on the home sites, sufficient separation between the adsorption system and the seasonal high groundwater can be achieved. Soil type 229D has not been irrigated and the iron staining is likely to be a relict of water sitting on top of low permeability clay. This soil type also has a percolation rate of 80 minutes per inch and will require special considerations when designing a domestic waste water disposal system. At the eastern end of the proposed development seven home sites are located near soil type X48. Vegetation on the ground surface suggested that shallow groundwater was present and excavation indicated that groundwater is present at a depth of 4.5 feet below the ground surface. Solutions for ensuring that at least four feet of separation is maintained between the base of the adsorption system and seasonal high groundwater include 1) installation of a pumped mounded adsorption system or 2) pumping leachate to adsorption systems located on ground without shallow groundwater located to the west of the impacted lots. This condition will impact up to seven home sites located adjacent to the X48 soil in the eastern part of the development. (d)(ii) Soil Percolation Tests Per DEQ Rules and Regulations Chapter 23, Section 7(d)(ii)(B), percolation tests are required for every third lot, or for each soil type as mapped by the Natural Resource Conservation Service (NRCS), whichever requires the least number of percolation tests. A total of 39 percolation test holes, three in each mapped soil type, were drilled to a depth of 36 inches within the proposed subdivision. The locations of the percolation test holes are provided on Figure 2. The test holes were all approximately three feet deep and the percolation tests were run on the bottom 18-24 inches of the hole. The percolation tests were performed in accordance with procedures set forth in DEQ Rules and Regulations Chapter 11, Part D, Appendix A. Approximately three inches of gravel was placed in the bottom of the holes and the holes were filled with 24-inches of water. After allowing the test holes to soak overnight, the percolation tests were performed, with fluid level measurements being conducted every 10 minutes. The percolation test sheets are contained in Appendix B. The percolation rates are summarized, by soil type, in Table 1. The fastest percolation rate was 5.3 minutes per inch in soil type 265AB. Two soils, 4A and 229D, located on the west side of the proposed development had percolation rates of 80 minutes per inch. These percolation rates do not meet the acceptable range of less than one minute per inch per Chapter 11 Part D Section 36 (d) or greater than 60 minutes per inch per Chapter 11 Part D Section 38 (b). Table 2 provides a summary of the slowest percolation rate for each soil type tested, as well as the soil loading rate and minimum square footage for an adsorption field using chamber system units. It is assumed that each home will have three bedrooms and a daily wastewater production rate of 450 gallons and that each chamber will have an equivalent area of 35.4 square feet. For the purpose of this analysis it is assumed that a bed layout will be used for the adsorption system.

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    4

    TABLE 2 PERCOLATION RATES, SOIL LOADING RATES,

    AND ADSORPTION FIELD SIZE SUMMARY TABLE

    SOIL TYPE

    SLOWEST PERCOLATION

    RATE (minutes per inch)

    SOIL LOADING RATE

    (gallons per day per square foot)

    MINIMUM ADSORPTION FIELD

    SIZE (square feet)

    4A

    80

    NA

    NA

    67A

    40

    0.35

    692

    200DE

    20

    0.46

    524

    229D

    80

    NA

    NA

    265AB

    8

    0.68

    355

    283

    40

    0.35

    692

    367CD

    40

    0.35

    692

    500

    16

    0.505

    486

    508

    40

    0.35

    692

    509

    40

    0.35

    692

    E33C

    26.6

    0.41

    580

    E67D

    20

    0.46

    524

    H36

    40

    0.35

    692

    X48

    No Testing

    NA

    NA

    NA= Not applicable - mounded adsorption system will be required. (d)(iii) Slopes of Lots Figure 3 is a detailed land surface slope map of the Sand Creek Ranch PUD. The slopes depicted on the map were computed from aerial photography ESRI DEM grid files from a digital terrain model with a resolution of six inch pixels. DEQ-WQD Rules and Regulations Chapter 11 Part D Section 36 (e)(i) indicates that for slopes of less than 15%, percolation rates must be between one and 60 minutes per inch and for percolation rates of between 46 and 60 minutes per inch the maximum slope allowed is 15%. There are 11 home sites in the western and south central part of the proposed development on which the surface slopes are between 12 and 15 percent. Six of the eleven home sites are adjacent to land with slopes of less than 12 percent on which adsorption systems could easily be located. These sites are on soil types 4A, 229D, and 508. The slowest percolation rate for soil types 4A and 229D, on which the other five home sites are located, were 80 minutes per inch, which exceeds the rate allowable for a conventional adsorption system; therefore, a mounded system will be required or leachate will have to be pumped to a more suitable location. Because the Sand Creek Ranch PUD will allow installation

  • NWESTON

    SCA

    LE1" = 1,070'

    SAN

    D C

    REEK

    RA

    NC

    HPU

    D A

    PPLICA

    TION

    LAN

    D SLO

    PE MA

    P FIG

    UR

    E 3

    SO

    UR

    CE

    : FOLE

    Y G

    RO

    UP

    GIS 2006

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    5

    of adsorption fields on property managed by the homeowners association, pumping leachate to a suitable location to the east where slopes are less steep is a likely solution. Johnson County requires that domestic waste water disposal systems be designed by a professional engineer, which will ensure that any adsorption system be designed to meet both DEQ and Johnson County standards. The slowest percolation rate for soil type 500 is 40 minutes per inch, which is suitable for slopes up to 20%. All adsorption systems will be set at least 15 feet from any break in slope that exceeds 15 degrees to meet DEQ Rules and Regulations Chapter 11 Part D Section 36 (e)(ii). (d)(iv) USGS Map Figure 1 is a 1:24,000 scale base map showing the water sheds, drainages, and water bodies both within the Sand Creek Ranch PUD and within one mile of its boundaries. The Sand Creek Ranch PUD lies within the watersheds of Sand Creek and French Creek. Eighty-nine home sites lie within the Sand Creek drainage, while the 10 home sites south of the Hopkins Ditch in the south central part of the proposed development lie within the French Creek drainage. While several of the home sites are near ephemeral drainages and the mainstem of Sand Creek, all adsorption systems will maintain adequate separation distances from bodies of water as required in DEQ Rules and Regulations Chapter 11 Part D Section 35 (a)(i). (d)(v) Replacement Adsorption System Area As indicated in Table 2, it is anticipated that the maximum square footage of an adsorption field for a three bedroom home at Sand Creek Ranch will be 692 square feet. A replacement field of the same size should be easily sited on the one acre lots each PUD will have. If site conditions do not allow for installation of a replacement adsorption system, then the replacement fields can be located on lands held in common with approval from the homeowners association. In the event that a four bedroom home is built on one of the lots, the corresponding adsorption system would have a square footage of 916 square feet. Both the adsorption system and a replacement system should fit on most lots, or could be located on the commonly owned property with approval from the homeowners association. (d)(vi & vi A) Population-Wastewater Type There are 99 single-family residential dwelling lots proposed in the Sand Creek Ranch PUD. Current plans anticipate that the vast majority of the housing units will have three bedrooms, with a few homes having two bedrooms and a few with four bedrooms. Although it is expected that many of the homeowners in the Sand Creek Ranch PUD will be retirees with two persons per home; however, for the purpose of facilities design it is assumed that there will be 3 persons per home. Using this assumption the maximum population of the development at build out is 297 persons. No commercial, industrial, or multiple use development will be allowed and generated wastewater will be domestic in nature. (d)(vii) Groundwater and Surface Water Protection (d)(vii)(A)(I-III) Geology The Sand Creek Ranch PUD lies on the Wasatch Formation. The Wasatch Formation consists of interbedded claystones, sandstones, conglomerates, and coal beds (Whitcomb and others, 1966). Whitcomb and others (1966) report that the Wasatch Formation is between 1,000 and 2,000 feet in northern Johnson County, but no wells for which lithologic logs are available in the vicinity of the Sand Creek Ranch PUD have been reported to fully penetrate the Wasatch Formation. Even with lithologic logs, determining the contact between the Wasatch Formation and the underlying Fort Union Formation can be difficult (Whitcomb and others, 1966). A coal bed methane gas well in Section 20, Township 51 North, Range 82 West (API Number 49-019-

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    6

    21128) was slated in 1999 to produce gas from a coal seam in the upper Fort Union Formation from a depth of 920 feet; however, the well was never drilled. According to geologic mapping by Hodson and others (1973) and Whitcomb and others (1966) there are no geologic structures, including faults, fractures, or karst features, in the area of the proposed development. The Wasatch Formation dips at 5 degrees to the east-northeast as measured on a sandstone outcrop in the SE Section 18, Township 51 North, Range 82 West. (d)(vii)(B)(I-IV) Groundwater Two distinct intervals of groundwater are encountered beneath the Sand Creek Ranch PUD. Shallow groundwater is observed at a small spring at an elevation of 4,920 feet in the NE NE Section 19, Township 51 North, Range 82 West and in a slough at an elevation of 4,850 feet in the SW SW Section 17, Township 51 North, Range 82 West. The spring in Section 19 was discharging between one and two gallons per minute on January 18, 2007. No water was observed moving at the slough in Section 19 and water only observed at a depth of 4.5 feet in a back hoe test pit. Although sandstones were not observed at either of these locations, it is likely that the source of the shallow groundwater is from drainage of a sandstone bed buried at a shallow depth. Five permitted water wells are located on the Sand Creek Ranch PUD. The wells vary in depth from 82 to 150 feet. Details for the wells in the Sand Creek Ranch PUD are summarized in Table 3 and copies of the statements of completion for the wells are provided in Appendix C. Jenkins #1 (U.W. 50073), which is 140 feet deep, has the highest production rate, of the five wells at 12 gallons per minute (gpm). The lithologic log for Jenkins #1 does not indicate that thick layers of shale or claystone overlay the production intervals (120-140 feet), but the fact that the well flows at the ground surface while the water is being produced from a depth of between 120 and 140 feet does indicate that the aquifer is confined. The statement of completion for Jenkins #3 (U.W. 42476), which is located a few hundred feet northeast of the Sand Creek Ranch PUD, is also included in Appendix C. The statements of completion and lithologic logs for U.W. 42726 and U.W. 62628 indicate that water is produced from sandstones and coal beds that underlie low permeability shales. The fact that the water levels in these two wells rises significantly above the production intervals indicates that the sandstones that yield water to the wells is confined. The low permeability shales prevent mingling of the shallow groundwater observed in the spring and slough from mixing with the deeper water. This is verified by the difference in water levels between the shallow groundwater and the water in the wells. An attempt was made to measure the water levels in the five Sand Creek Ranch water wells. A water level could not be obtained from Jenkins #1 because the well flows when it is not pumped and the wellhead is sealed. The water in Camino #2 was frozen at the ground surface, which prevented measurement of the water level. The water levels measured in the remaining three wells and the results are provided in Table 3. Water levels have not been routinely measured in the wells therefore the seasonal variations in water levels is not known. In a memorandum written by the State Engineers Office on August 26, 1985, water levels were measured in several area wells to investigate whether water levels had declined. The summer season water levels were found to be somewhat lower than water levels reported on statements of completion, but the decreases in water levels were attributed to increased lawn irrigation. A copy of the memorandum is contained in Appendix C attached to the statement of completion for U.W. 27905. (d)(vii)(C) Aquifer Classification (d)(vii)(C)(I) State Engineer Well Search The Wyoming State Engineers Office database was accessed from the internet on December 13, 2006 to conduct an inventory of permitted water wells located within one mile the proposed

  • TAB

    LE 3 SA

    ND

    CR

    EEK R

    AN

    CH

    PUD

    EXISTIN

    G W

    ELLS SUM

    MA

    RY

    SEO

    PERM

    IT N

    UM

    BER

    LO

    CA

    TION

    *

    WELL N

    AM

    E

    WELL

    ELEVATIO

    N

    (feet, asl)

    TO

    TAL

    DEPTH

    (feet)

    STA

    TIC

    WA

    TER

    LEVEL (feet)***

    PR

    OD

    UC

    ING

    IN

    TERVA

    L (feet)

    YIELD

    (gpm

    )

    ELEVATIO

    N

    OF STA

    TIC

    WA

    TER

    LEVEL (feet, asl)

    19271

    S

    WS

    E 18, 51, 82

    C

    amino #2

    4,920

    135

    U

    nknown

    U

    nknown

    3

    Unknow

    n

    19272

    NE

    SE

    18, 51, 82

    Cam

    ino #3

    4,890

    150

    3.5

    Unknow

    n 1

    4,886.5

    19273

    N

    ES

    W 19, 51, 82

    H

    euermann #1

    5,043

    145

    10

    Unknow

    n 5

    5,033

    50073

    S

    WS

    W 17, 51, 82

    Jenkins #1

    4,860

    140

    U

    nknown**

    120-140

    12

    Unknow

    n

    62628

    SW

    SE

    18, 51, 82

    Jenkins Ranch #2

    4,930

    82 17

    62-82

    8

    4,913 *

    , S

    ection, Township, R

    ange, ** Well flow

    s when not being pum

    ped, ***Water levels m

    easured 1/10/07, Cam

    ino #2 frozen

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    7

    development boundary. A copy of the well search is contained in Table 4. The locations of the wells are plotted by quarter-quarter section. In many quarter-quarter sections the wells are too numerous to plot, therefore Figure 4 contains each section divided into quarter-quarters and the number of wells present in that area. (d)(vii)(C)(II-III) Groundwater Class Water samples were collected from the spring in the NE NE Section 19 and from Jenkins #1 for submission to an EPA certified laboratory for analysis. The analyses on each source were performed for the constituents listed in DEQ Rules and Regulations Chapter 8 Table 1, for determining the class of underground water. The results of the water quality sampling are summarized in Table 4 and copies of the analytical reports are provided in Appendix D. During sampling, the sample from the well was mistakenly identified as being from Jenkins Well No. 3, when in fact is was collected from Jenkins #1. Comparison of the results of the analyses demonstrate, that with the exception of pH, water from the confined aquifer which Jenkins #1 taps meets all the standards for Class I water. The pH of 6.13 standard units is below the lower threshold of 6.5 standard units. No nitrates or nitrates were detected in the well water. The spring in Section 19 is not developed and is therefore not sanitary, which accounts for the bacterial contamination observed in the laboratory results. Comparison of the results of the water quality analyses from the spring to the standards set by DEQ indicates that the water does not meet the requirements for either Class I or Class II water. The spring water exceeds the concentration of aluminum for Class II water, the hydrogen sulfide (as sulfide) for Class I water, the iron concentration for both Class I and Class II water, the manganese concentration for both Class I and Class II water, the oil and grease concentration for Class I water, the phenol concentration for Class I water, and the gross alpha concentration for both Class I and Class II water. (d)(vii)(D)&(d)(viii) Septic System Models The DEQ-WQD Chapter 23 Appendix A, Wehrmann Nitrate Model was used to estimate the cumulative nitrate loading from the proposed Sand Creek Ranch PUD. In an effort to be conservative in this modeling effort the Wehrmann model was run for all 99 lots of the subdivision. The quantity of infiltration used in the model was estimated to be from precipitation. The Wyoming water resources data system reports that the Buffalo area received an average of 15 inches of precipitation between 1971 and 2000. Because Wyomings climate is dry it is assumed that only 10-percent of precipitation infiltrates into the ground and reaches the vadose zone. The total acreage of the subdivision is 850 acres and for the purposes of this model it is assumed that the homes will have an average of three bedrooms. The hydraulic conductivity or K value was estimated from percolation testing. Six of the 13 tested soil types had percolation rates of 40 minutes per inch, which yields an estimated hydraulic conductivity of 3.0 feet per day. Using this value maximized the models nitrate output resulting in a worst-case scenario. The hydraulic gradient was calculated using a three point solution based on the water levels and elevations of the water wells with State Engineers Office permit numbers U.W. 19273, 62628, and 32622. Although these wells produce water from the confined aquifer the consistent dips of the formations make it likely that shallow groundwater will either follow the same gradient or follow the surface topography. The calculated hydraulic gradient is 0.037 feet per foot in a direction of North 33 degrees East. It was assumed that each lot would have one-half acre of irrigated lawn per lot, although actual irrigated acreage will likely be only one-quarter acre per lot. The ambient nitrate levels were obtained from the water quality analyses, which were non-detect. Based on these inputs the model predicts that the 99 lots will result in a total cumulative nitrate load of 1.0 mg/L, which is a full order of magnitude lower than the 10 mg/L maximum concentration allowed in the WDEQ Chapter 23 Rules and Regulations.

  • SAND CREEK RANCHPUD APPLICATION

    WELL LOCATION MAP FIGURE 4

    N

    WESTON

    SCALE

    SEO PERMITTED WELL LOCATIONSSEE TABLE 5.

    6 8

    9 5 8 15

    12 6 5

    6

    8

    9

    8

    3

    SAND CREEK RANCH BOUNDARY

    131021

    116311

    116312

    18099

    66097

    56422

    10344030475

    103426

    21917

    109499

    161195

    121610

    110960

    113818

    147016

    118663

    5225155143

    17458

    116590

    86346

    125132

    114708

    13005432381

    103158

    85250

    64852

    95361

    12545662628

    19271 18728

    42726

    19272

    19273

    35/8/191 48643

    84853

    11630739/2/94

    7626

    169420

    169419131024

    13724

    29737361

    15108125738

    16043

    39/2/1703266246248

    1465

    2833011777311842832522

    341941447971020032608811857

    43602116304

    27902

    15108 SEO PERMITTED WELL LOCATION AND PERMIT NUMBER

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    8

    WDEQ Chapter 23 Appendix B, Minimum isolation distance was used to calculate the vertical travel time and 2 year horizontal travel time for each lot. The vertical travel time is calculated to be 89 days based on 315 inches for AP and the total volumetric soil moisture was estimated from the Table 1 provided by WDEQ. The depth to seasonal high groundwater was estimated to be 10 feet, which was indicated from most of the soil test pits on the site. The two year horizontal time of travel distance is calculated to be 712 feet, based on inputs of 3 feet/day for K, a hydraulic gradient of 0.037 feet/foot and an effective porosity of 10-percent. This predict indicates that neighboring properties should not be affected by wastewater disposal from the Sand Creek Ranch PUD and that what little fluid may leave the property will have an estimated nitrate concentration of 1 mg/L.

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    9

    TABLE 4 WATER QUALITY SAMPLING RESULTS

    SEO Permit Number

    Water Quality Standard

    Class I Water*

    Water Quality Standard

    Class II Water*

    Jenkins # 1 U.W. 50073

    Spring NE NE Section 19

    Total Depth (feet)

    -

    -

    140

    Ground Level

    Formation - - Wasatch Wasatch Date Collected - - 1/11/07 1/18/07

    Aluminum (mg/L)

    -

    5.0

    ND

    7.4

    Ammonia (mg/L)

    0.5

    -

    0.09

    0.30

    Arsenic (mg/L) 0.05 0.1 ND 0.004 Barium (mg/L) 1.0 - ND 0.3 Boron (mg/L) 0.75 0.75 ND 0.2

    Cadmium (mg/L)

    0.01

    0.01

    ND

    ND

    Chloride (mg/L) 250 100.0 9 4 Chromium

    (mg/L)

    0.05

    0.1

    ND

    ND Copper (mg/L) 1.0 0.2 ND ND Cyanide (mg/L) 0.2 - ND ND Fluoride (mg/L) 1.4-2.4 - 0.1 0.2

    Hydrogen Sulfide (mg/L)

    0.05

    -

    ND

    11.4

    Iron (mg/L) 0.3 5.0 ND 42.1 Lead (mg/L) 0.05 5.0 ND ND Manganese

    (mg/L)

    0.05

    0.2

    0.01

    0.79 Mercury (mg/L) 0.002 - ND ND

    Nitrate as N (mg/L)

    10

    -

    ND

    ND

    Nitrite as N (mg/L)

    1.0

    -

    ND

    ND

    Oil and Grease Virtually Free 10.0 ND 6.5 Phenol (mg/L) 0.001 - ND 0.027

    Selenium (mg/L) 0.01 0.02 ND ND Silver (mg/L) 0.05 - ND ND

    Sulfate (mg/L) 250 200.0 96 108 Total Dissolved Solids (mg/L)

    500 2000.0 318 446

    Uranium 5.0 5.0 ND 0.0292 Zinc (mg/L) 5.0 2.0 0.08 0.03

    pH (S.U.) 6.5 8.5 4.5-9.0 6.13 7.84 Gross Alpha

    (pCi/L)

    15

    15

    ND

    30.2 +/-1.6 *Source DEQ-WQD Chapter 8, Table 1. ND = NOT DETECTED

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    10

    CHAPTER 23 - SECTION 8 (a)(i) Type of Water Supply The water supply needs for the Sand Creek Ranch PUD will be met with on-site wells. It is anticipated that individual wells will be drilled to meet the needs of each lot owner. As stated above, if water supply wells need to be drilled off of the one-acre fee lots to meet minimum offsets from wastewater disposal facilities and adsorption system replacement reservations, then the lot owners will have the ability to site wells on the lands owned in common. It may be preferable to have groups of homes share a common water well. Up to three homes can be connected to a single well and remain a domestic water well under the State Engineers Office rules and regulations. Installation of a common well to be shared among homeowners would require installation of storage facilities and booster pumps to each home. Figures 5 and 6 are generic designs, previously approved by DEQ-WQD, for storage and distribution systems for three homes sharing a water well within a subdivision. Minor adjustments to this design could be required for site specific conditions and to account for actual production of the water well. Any such system should be designed by a professional engineer. (a)(ii) Average and Maximum Water Usage It is assumed that the 99 lots will have an average population of 3.5 persons. The build-out population of the Sand Creek Ranch PUD, if a home is built on each lot, will be 347 persons. DEQ-WQD Rules and Regulations Chapter 12 Section 8 (a) states that a design rate 125 gallons per day per person can be used for an average daily demand and a rate of 340 gallons per day per person can be used for a peak day demand if no consumption data are available. Application of these per capita demands to the build out population of 347 persons results in an average daily demand of 43,375 gallons (30 gpm) and a peak daily demand of 117,980 gallons (82 gpm). Sand Creek Ranch has territorial surface water rights that will be transferred to the Sand Creek Ranch PUD homeowners association. Water rights on the individual 99 fee lots will be managed for each lot by the homeowners association. The Sand Creek Ranch PUD will have an irrigation system that allows for lawn watering for use by the home owners using a portion of the appropriated water rights. Architectural covenants will limit the size of irrigated lawns and lots will have up to 500 gallons per day for watering from the surface water source. This supplemental source of supply will serve to significantly reduce the peak daily demand on the potable water supply sources; therefore, the actual peak daily demand will be lower than the 82 gpm projected above. (a)(iii) Water Well - Septic System Compatibility As described previously, water wells drilled to depths below 80 feet exhibit a significant degree of confinement and leachate from septic systems is not likely to migrate into the sandstones yielding drinking water to wells. Furthermore, the nitrate modeling indicates that in a worst-case scenario the nitrate concentrations could rise by only one mg/L. Since the confined aquifer beneath the Sand Creek Ranch PUD has an effective nitrate concentration of 0 mg/L, the model predicts that the nitrate concentration would be far below the maximum contaminant level of 10 mg/L. (a)(iv) Surface and Groundwater Rights Currently several surface water and groundwater rights are held by Sand Creek Ranch. Table 3 provides details of the permitted wells for which rights are held by Sand Creek Ranch. Copies of the statements of completion are provided in Appendix C. A water rights inventory was compiled by Mr. Frank Carr of Water Right Services in 2004. The report provided by Mr. Carr is provided in Appendix F. Sand Creek Ranch will be transferring all existing water rights to the Sand Creek Ranch PUD for management for use by the ranch community.

  • SAN

    D C

    REEK

    RA

    NC

    HPU

    D A

    PPLICA

    TION

    STOR

    AG

    E / PUM

    P CO

    NTR

    OL VA

    ULT D

    ETAILS

    FIGU

    RE 5

    SCA

    LE1" = 2'

    WA

    TTS 742-2

    CH

    EC

    K V

    ALVE

    BALL VALV

    E

    STE

    EL R

    UN

    GSTE

    PS IN

    TO V

    AULT (2)

    LIGH

    T INSEA

    LED

    GLO

    BEPU

    MP C

    ON

    TRO

    LB

    OX C

    IRC

    UIT BR

    EAKER

    BO

    X

    24-INC

    HFR

    OS

    T-FRE

    EM

    ANW

    AYS (2)

    BR

    AS

    S U

    NIO

    N

    40 / 70 #P

    RE

    SS

    UR

    ESW

    ITCH

    0 - 100 #P

    RE

    SS

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    E G

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    RE

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    ENSIO

    NS

    HE

    IGH

    T = 8 FEE

    TLE

    NG

    TH = 8 FEE

    TW

    IDTH

    = 6 FEE

    T

    1,000 WA

    TTH

    EA

    TER

    BALL VALV

    E

  • SAN

    D C

    REEK

    RA

    NC

    HPU

    D A

    PPLICA

    TION

    SCH

    EMA

    TIC D

    ISTRIB

    UTIO

    N PIPELIN

    E DIA

    GR

    AM

    FIGU

    RE 6

    1 1/4-INC

    HH

    DP

    E LIN

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    RE

    SID

    EN

    CE

    S

    1 1/4-INC

    H H

    DP

    E LIN

    EFR

    OM

    WE

    LL

    STOR

    AG

    E AN

    DPU

    MP C

    ON

    TRO

    LV

    AU

    LT

    RE

    SID

    EN

    CE

    RE

    SID

    EN

    CE

    RE

    SID

    EN

    CE

    10 GP

    M FLO

    W R

    ES

    TRIC

    TOR

    WATTS 742-2 C

    HE

    CK VALVE

    MU

    LLER

    MA

    RK

    II CU

    RB

    STO

    P

    10 GP

    M FLO

    W R

    ES

    TRIC

    TOR

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    HE

    CK VALVE

    MU

    LLER

    MA

    RK

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    RB

    STO

    P

    10 GP

    M FLO

    W R

    ES

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    HE

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    MU

    LLER

    MA

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    II CU

    RB

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    WE

    LL

    TEE

    FITTING

    TEE

    FITTING

    NO

    SCA

    LE

    SEE DETA

    ILSIN

    FIGU

    RE 5

  • Site Suitability for Individual Water Supply And Wastewater Systems Sand Creek Ranch Planned Unit Development, Johnson County Wyoming

    11

    (a)(v) Mitigation of Impacts To date there have been no documented impacts to surrounding property owners as a function of groundwater withdrawals. It is not anticipated that impacts will occur as a result of developing a groundwater supply for the 99 lots on the Sand Creek Ranch PUD. The potential for further impact is further lessened by the ability of the Sand Creek Ranch PUD to use existing surface water irrigation rights to meet peak day demands on potable water that are a result of limited lawn watering. If impacts are proven to be the result of this subdivision, the homeowners would be forced to reduce water usage, and/or drill wells deeper, such that they are not all impacting the same production intervals. (b) Connection to Existing Water Supply System This section is not applicable to the Sand Creek Ranch PUD because individual water wells will be used to meet the water demands of the residents. (c) Common Water Supply System This section is not applicable to the Sand Creek Ranch PUD because individual or clustered water wells will be used to meet the water demands of the residents. (d) Groundwater Quantity and Quality As detailed in Table 3, the five water wells are located on the Sand Creek Ranch PUD yield between one and 12 gpm. A review of Table 5, the permitted water well summary table, indicates that 100 wells in the vicinity yield between 10 and 20 gpm. A well with a capacity of five gpm will provide adequate water for a single family dwelling, especially if irrigation of lawns is partially satisfied with surface water. Whitcomb and others (1966) documented a pump test on a well in the SE SE Section 33, Township 51 North, Range 82 West, which is approximately two miles southeast of the Sand Creek Ranch PUD. The well was pump tested at 70 gpm for four hours with 46 feet of drawdown. The specific capacity was computed to be 1.5 gpm per foot of drawdown. These well data indicate that the likelihood of obtaining adequate quantities of water for the Sand Creek Ranch PUD is excellent. The overall quality of water from Jenkins #1 is very good, as demonstrated in Table 4. The TDS is well below the recommended level of 500 mg/L. The only deviation from the standards for a public water supply source is the pH, which is slightly below the minimum standard of 6.5 standard units. Similar qualities can be expected from wells drilled to similar depths.

  • TAB

    LE 5STA

    TE ENG

    INEER

    'S OFFIC

    E WELL D

    ATA

    BA

    SE SEAR

    CH

    Perm

    it #P

    riority

    Status

    Township

    Range

    Section

    Qtrqtr

    LotsA

    pplicant

    Facility Nam

    eU

    sesY

    ld A

    ctW

    ell D

    epthStatic D

    epthM

    wbz

    TopM

    wbz

    Bottom

    P143021W3/4/2002

    GSI

    5182

    7SESW

    JOY E. ED

    WAR

    DS/JAN

    IS L. H

    ARRIS

    EDW

    ARD

    S/HAR

    RIS #

    1D

    OM

    P154071W9/12/2003

    GSI

    5182

    7N

    ESWL1

    TIMO

    THY S &

    LORI L KALU

    SKALU

    S #1

    DO

    M,ST

    O

    P161194W8/4/2004

    GSI

    5182

    7SW

    NW

    CHAR

    LES IRIG

    ARAY &

    CARO

    L SN

    OBE L

    CARO

    LINA #

    2D

    OM

    ,STO

    P168942W7/13/2005

    GSI

    5182

    7SW

    SWSU

    E & BU

    D LED

    BETTERLED

    BETTER W

    ELL #1

    DO

    MP103158W

    7/29/1996G

    ST51

    827

    NW

    SER.C. R

    OBIN

    SON

    RO

    BINSO

    N #

    2D

    OM

    3520

    104475

    525P110960W

    7/20/1998G

    ST51

    827

    SWSW

    FTP PARTN

    ERSH

    IPArk #

    2D

    OM

    8280

    55250

    275

    P113818W1/27/1999

    GST

    5182

    7SW

    S WBO

    B COM

    PTON

    MIKEY #

    1D

    OM

    9360

    55U

    nknown

    Unknow

    nP114708W

    3/24/1999G

    ST51

    827

    SESWL4

    KIM/U

    RSU

    LA SCHW

    IRIAN

    SCHW

    IRIAN

    #1

    DO

    M10

    32035

    240320

    P116590W6/21/1999

    GST

    5182

    7SEN

    WKEN

    BURTO

    NKEN

    BURTO

    N #

    1D

    OM

    20100

    20U

    nknown

    Unknow

    n

    P121610W12/20/1999

    GST

    5182

    7N

    WSW

    MILLER

    SAND

    CREEK R

    ANCH

    , LLC

    MILLER

    #3

    DO

    M,ST

    O7

    2207

    130210

    P125132W4/27/2000

    GST

    5182

    7SESW

    L12KELLY D

    . & G

    EORG

    IA A. RICE

    RICE 1

    DO

    M12

    12020

    Unknow

    nU

    nknown

    P130054W10/18/2000

    GST

    5182

    7SESW

    L3SH

    AWN

    /MICH

    ELLE WELSH

    WELSH

    # 1

    DO

    M15

    52055

    Unknow

    nU

    nknown

    P155143W11/19/2003

    GST

    5182

    7N

    ENW

    FLOYD

    D &

    LORI L. CU

    MM

    ING

    SCU

    MM

    ING

    S #1

    DO

    M4

    24026

    195225

    P161195W8/4/2004

    GST

    5182

    7SW

    NW

    CHAR

    LES IRIG

    ARAY &

    CARO

    L SN

    OBE L

    CARO

    LINA #

    1D

    OM

    1060

    40U

    nknown

    Unknow

    n

    P17458W12/27/1972

    GST

    5182

    7SEN

    WM

    ARSH

    ALL D. JEN

    KINS

    JENKIN

    S #1

    DO

    M,ST

    O10

    29060

    225244

    P32381W3/3/1976

    GST

    5182

    7SW

    SECLAIR

    & ELO

    GEN

    E P. RO

    BINSO

    NPIER

    SON

    #

    DO

    M3

    260260

    Unknow

    nU

    nknown

    P5225W4/6/1970

    GST

    5182

    7N

    ENW

    EDVIG

    O &

    HELEN

    G. W

    INTH

    ERW

    INTH

    ER #

    1D

    OM

    6220

    31185

    220

    P85250W5/31/1991

    GST

    5182

    7SW

    NE

    R. TR

    ACY RH

    OD

    ESR. T. R

    HO

    DES #

    1D

    OM

    ,STO

    10124

    1896

    116

    P86346W10/9/1991

    GST

    5182

    7SEN

    WTH

    OM

    AS AND

    BARBAR

    A D

    ENN

    ISON

    BLUEBIR

    D #

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    10260

    220220

    260P109570W

    4/10/1998U

    NA

    5182

    7N

    ENW

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    RY &

    /OR VED

    A M. BAU

    ERH

    ILLTOP #

    1 WELL

    DO

    M

    P165070W2/2/2005

    GSI

    5182

    8SESE

    DAVE R

    EDD

    RO

    CK CREEK M

    EADO

    WS

    #3

    TST

  • TAB

    LE 5STA

    TE ENG

    INEER

    'S OFFIC

    E WELL D

    ATA

    BA

    SE SEAR

    CH

    Perm

    it #P

    riority

    Status

    Township

    Range

    Section

    Qtrqtr

    LotsA

    pplicant

    Facility Nam

    eU

    sesY

    ld A

    ctW

    ell D

    epthStatic D

    epthM

    wbz

    TopM

    wbz

    Bottom

    P165071W2/2/2005

    GSI

    5182

    8SW

    NW

    DAVE R

    EDD

    RO

    CK CREEK M

    EADO

    WS

    #1

    TST

    P165072W2/2/2005

    GSI

    5182

    8SW

    SED

    AVE RED

    DRO

    CK CREEK M

    EADO

    WS

    #2

    TST

    P16243P12/31/1967

    GST

    5182

    8SEN

    EALVA TAYLO

    R**G

    EORG

    E TAYLO

    RTAYLO

    R #

    3D

    OM

    ,STO

    5900

    -4U

    nknown

    Unknow

    n

    39/10/163W7/12/2006

    UN

    A51

    828

    NESE

    DAW

    SON

    CON

    STRU

    CTION

    , INC.

    DAW

    SON

    WELL #

    1D

    OM

    39/10/89W6/12/2006

    UN

    A51

    828

    NESE

    SEAN &

    LYNETTE D

    URRAN

    TS &

    L DU

    RRAN

    T WELL

    #1

    DO

    M39/4/307W

    9/25/2006U

    NA

    5182

    8SW

    SEJO

    HN

    & CATH

    ERIN

    E DESCH

    DESCH

    #1

    DO

    M39/5/173W

    7/18/2006U

    NA

    5182

    8N

    ESWD

    AN &

    MO

    NICA D

    AUG

    HER

    TYD

    AUG

    HER

    TY #1

    DO

    M39/5/186W

    7/26/2006U

    NA

    5182

    8N

    ESWM

    ICHAEL J. CECELIA L IH

    NAT

    CECE #1

    DO

    M39/8/78W

    6/7/2006U

    NA

    5182

    8SW

    NW

    MICH

    AEL J. CECELIA L IHN

    ATCECELIA #

    1D

    OM

    P104525W11/21/1996

    GST

    5182

    16N

    ENE

    GLEN

    MEAN

    SG

    LEN M

    EANS #

    4D

    OM

    14160

    2140

    160

    P16043P4/30/1955

    GST

    5182

    16SW

    SWREEVES IN

    C.RO

    BINSO

    N #

    1STO

    15220

    -1U

    nknown

    Unknow

    n

    P95286W5/5/1994

    GST

    5182

    16N

    WN

    ED

    ELTON

    AND

    CARO

    L A. H

    ERM

    ANH

    ERM

    AN #

    1D

    OM

    16123

    1095

    119

    P28330W10/8/1974

    ADJ

    5182

    17SESW

    CARL H

    . LARSO

    NLAR

    SON

    #1

    STO,IRR

    ,DO

    M40

    250150

    140250

    P42392W3/14/1978

    ADJ

    5182

    17N

    WN

    ELAN

    NY R

    . PETERSO

    N**PAU

    LA M

    . PETERSO

    NPETER

    SON

    #3

    DO

    M20

    26070

    240260

    P159882W6/1/2004

    GSE

    5182

    17SW

    NW

    DO

    NALD

    M/TIN

    A A SEALSSEALS #

    3D

    OM

    ,STO

    P159883W6/1/2004

    GSE

    5182

    17SW

    NW

    DO

    NALD

    M/TIN

    A A SEALSSEALS #

    4D

    OM

    ,STO

    P173012W2/6/2006

    GSI

    5182

    17N

    ENW

    GREG

    ORY LAU

    VERLAU

    VER #

    1D

    OM

    P100049W8/15/1995

    GST

    5182

    17N

    WSE

    L14RICH

    ARD

    B/MAR

    Y ANN

    BAYERS

    BAYERS #

    1D

    OM

    10220

    60180

    220

    P102003W4/8/1996

    GST

    5182

    17N

    ENW

    L15,BM

    ATTHEW

    HEN

    RY

    LON

    GH

    ORN

    #3

    DO

    M10

    12030

    80120

    P104511W11/14/1996

    GST

    5182

    17SEN

    WL1,B2

    JAMES A/O

    R FLO

    REN

    CE E LON

    GLO

    NG

    #1

    DO

    M,ST

    O6

    134

    411

    P106818W7/24/1997

    GST

    5182

    17N

    WN

    WL13

    ORLEN

    L FYOCK

    FYOCK #

    1D

    OM

    20212

    3200

    205

  • TAB

    LE 5STA

    TE ENG

    INEER

    'S OFFIC

    E WELL D

    ATA

    BA

    SE SEAR

    CH

    Perm

    it #P

    riority

    Status

    Township

    Range

    Section

    Qtrqtr

    LotsA

    pplicant

    Facility Nam

    eU

    sesY

    ld A

    ctW

    ell D

    epthStatic D

    epthM

    wbz

    TopM

    wbz

    Bottom

    P116304W6/16/1999

    GST

    5182

    17N

    ESWL26

    GAR

    Y L FOSTM

    EIER/BAR

    BARA

    SCHN

    ACHTEN

    BERG

    ER AS JO

    INT

    TENAN

    TSCH

    AMBER

    LAIN #

    1D

    OM

    15275

    150U

    nknown

    Unknow

    n

    P116305W6/16/1999

    GST

    5182

    17SEN

    EW

    ILLIAM CH

    RISTEN

    SENCH

    RISTEN

    SEN #

    1STO

    10100

    40U

    nknown

    Unknow

    n

    P116306W6/16/1999

    GST

    5182

    17SEN

    EW

    ILLIAM CH

    RISTEN

    SENCH

    RISTEN

    SEN #

    2STO

    25300

    10U

    nknown

    Unknow

    n

    P117773W7/26/1999

    GST

    5182

    17SESW

    TED/D

    ARLEN

    E CRISM

    ANCR

    ISMAN

    WELL N

    O. 1

    DO

    M,S T

    O7

    20025

    Unknow

    nU

    nknown

    P117993W7/23/1999

    GST

    5182

    17N

    WN

    ERobert/Jean Zabloudil

    ZAB 31D

    OM

    16259

    28U

    nknown

    Unknow

    nP117999W

    7/30/1999G

    ST51

    8217

    SENE

    L29G

    ary/Cecelia Walters

    WALTER

    S #1

    DO

    M18

    28045

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    10130

    -4120

    130P152141W

    7/2/2003G

    SE51

    8218

    NEN

    WL1

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    entonAllim

    ax #1-2

    DO

    M

    P95361W5/16/1994

    GSE

    5182

    18SEN

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    NU

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    LASPIS ALASPISA #

    1D

    OM

    P118663W9/2/1999

    GST

    5182

    18N

    WN

    WCH

    ARLES A/M

    ILDRED

    I WAG

    NER

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    6200

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    P125456W5/11/2000

    GST

    5182

    18SESW

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    12500

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    nP135624W

    6/13/2001G

    ST51

    8218

    NEN

    EL23

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    LIVEZEYLIVEZEY #

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    19220

    6115

    150P147016W

    9/17/2002G

    ST51

    8218

    NW

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    MILLS #

    1D

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    10325

    85310

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    P15086W8/21/1972

    GST

    5182

    18SW

    NE

    MICH

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    M

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    ARK #

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    8182

    22162

    181P157041W

    3/15/2004G

    ST51

    8218

    SENE

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    E BUSTER

    #1

    DO

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    105160

    P163337W10/25/2004

    GST

    5182

    18N

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    DAN

    IEL J & KR

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    DO

    M6

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    250360

    P19271P12/31/1942

    GST

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    18SW

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    . JENKIN

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    P19272P12/31/1942

    GST

    5182

    18N

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    . JENKIN

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    INO

    #3

    STO1

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    nU

    nknown

    P40707W9/1/1977

    GST

    5182

    18N

    ENE

    CHAR

    LES C. & D

    ON

    NA KAYE &

    RU

    SSELL L. OLD

    SCAM

    PBELL #1

    DO

    M25

    26025

    140260

    P42726W3/30/1978

    GST

    5182

    18N

    ESEL2

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    ANCY J SCH

    ETTIGJEN

    KINS #

    3D

    OM

    20260

    -4U

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    n

    P43663W5/31/1978

    GST

    5182

    18SEN

    EM

    ILAR F. &

    EVELYON

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    WILLIAM

    SVEN

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    #2

    DO

    M10

    200190

    190200

    P44520W8/7/1978

    GST

    5182

    18SEN

    ED

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    DIN

    GTO

    NAD

    DIN

    GTO

    N #

    1D

    OM

    10285

    5220

    255P44731W

    8/31/1978G

    ST51

    8218

    SENE

    JAY DEAN

    WILSO

    NW

    ILSON

    #1

    DO

    M15

    187-4

    80187

    P47707W4/27/1979

    GST

    5182

    18SEN

    ETIM

    AND

    GABR

    IELLE GAR

    BW

    ILD BO

    RE #

    1D

    OM

    12160

    -4140

    155

  • TAB

    LE 5STA

    TE ENG

    INEER

    'S OFFIC

    E WELL D

    ATA

    BA

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    CH

    Perm

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    P58766W10/27/1981

    GST

    5182

    18N

    ENE

    L8D

    ANIEL J &

    KRISTIN

    E L THIELE

    TENN

    ESSEE #8

    DO

    M6

    4520

    3045

    P61944W9/7/1982

    GST

    5182

    18N

    ENE

    GLEN

    A. JENKIN

    SJESSE #

    1D

    OM

    9220

    26160

    220

    P62628W11/30/1982

    GST

    5182

    18SW

    SEELIZABETH

    R. JEN

    KINS

    JENKIN

    S RAN

    CH #

    2STO

    882

    40U

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    n

    P64852W7/27/1983

    GST

    5182

    18N

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    EM

    ICHAEL C. &

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    ALTERD

    IAMO

    ND

    #1

    DO

    M6

    170100

    150170

    P65427W9/14/1983

    GST

    5182

    18N

    ENE

    GLEN

    A. JENKIN

    SRU

    STY #1

    DO

    M5

    10025

    95100

    P65428W9/14/1983

    GST

    5182

    18N

    ENE

    ALBERT I. AN

    D N

    ORM

    A F. EDD

    YFR

    EEDO

    M #

    1D

    OM

    6200

    55190

    200

    P94754W3/7/1994

    GST

    5182

    18SW

    NE

    BLAIR KLEIN

    WIN

    D M

    ILL #1

    DO

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    16055

    135155

    P94755W3/7/1994

    GST

    5182

    18SEN

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    DO

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    24060

    200235

    39/3/79W6/7/2006

    UN

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    8218

    NW

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    H. R

    ICHAR

    D SO

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    SON

    LUCKY #

    3D

    OM

    P84260W1/16/1991

    UN

    A51

    8218

    NEN

    EL21

    JOH

    N C. AN

    D JAN

    E F. RYH

    TIVER

    PLANCKE #

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    OM

    P19273P12/31/1952

    GST

    5182

    19N

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    . JENKIN

    SH

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    N #

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    5145

    -4U

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    nP169420W

    8/9/2005G

    SI51

    8220

    SESEG

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    P116307W6/16/1999

    GST

    5182

    20SW

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    160-4

    140160

    P125738W8/6/1999

    GST

    5182

    20N

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    DO

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    20045

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    nU

    nknown

    P131024W11/29/2000

    GST

    5182

    20N

    WSE

    RICH

    ARD

    J / KATHY L

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    Y LEE # 1

    DO

    M25

    3750

    350367

    P13724P6/21/1962

    GST

    5182

    20N

    WSE

    RICH

    ARD

    J/KATHY L

    VERPLAN

    CKEJ &

    J CON

    WAY #

    1D

    OM

    ,STO

    25390

    305305

    390

    P1465W4/6/1965

    GST

    5182

    20N

    ENW

    J. CRAIG

    AND

    DO

    NN

    A M. SM

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    #1

    DO

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    310-6

    294306

    P29737W4/24/1975

    GST

    5182

    20SEN

    ECLAR

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    WILM

    A COLE

    COLE #

    1D

    OM

    10180

    16U

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    nP32662W

    3/22/1976G

    ST51

    8220

    NEN

    WJO

    SEPH SILBER

    NAG

    ELSILBER

    NAG

    EL #1

    DO

    M16

    14033

    100140

    P361W4/17/1958

    GST

    5182

    20SW

    NE

    A.J. BARKER

    BARKER

    #2

    STO200

    60200

    P46248W6/23/1978

    GST

    5182

    20N

    ENW

    RAYM

    ON

    D L. &

    BERN

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    **DAVID

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    MO

    RG

    ANTO

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    #1

    DO

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    10035

    80100

    39/2/170W7/14/2006

    UN

    A51

    8220

    NEN

    WCR

    AIG &

    DO

    NN

    A SMITH

    SMITH

    #1

    DO

    M

  • TAB

    LE 5STA

    TE ENG

    INEER

    'S OFFIC

    E WELL D

    ATA

    BA

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    CH

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    P762G2/27/1958

    UN

    A51

    8220

    SESEAR

    THU

    R J. &

    MAR

    GAR

    ET M.

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    BEYDLER

    #1

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    M180

    140-6

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    nU

    nknown

    P169419W8/9/2005

    GSI

    5182

    21N

    WSW

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    ELEN M

    ATHES

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    ES #3

    STOP15108P

    9/2/1955G

    ST51

    8221

    NW

    NW

    WAR

    REN

    D. ATTER

    ATTER #

    1STO

    3120

    20100

    12038/4/555W

    4/4/2006U

    NA

    5182

    21N

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    ATTERATTER

    RAN

    CH #

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    IS39/2/94W

    6/14/2006U

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    5182

    21SW

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    ES #4

    STOP84853W

    4/8/1991G

    ST51

    8229

    SWN

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    ARCIE M

    CSTAYM

    . MCSTAY #

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    OM

    5380

    358360

    380P84853W

    4/8/1991G

    ST51

    8229

    SWN

    WM

    ARCIE M

    CSTAYM

    . MCSTAY #

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    5380

    358360

    380P84853W

    4/8/1991G

    ST51

    8229

    SWN

    WM

    ARCIE M

    CSTAYM

    . MCSTAY #

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    5380

    358360

    380P48643W

    6/12/1979G

    ST51

    8230

    NW

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    JOH

    N D

    . & PH

    YLLIS J. HALL

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    2STO

    8140

    40120

    130P48643W

    6/12/1979G

    ST51

    8230

    NW

    NE

    JOH

    N D

    . & PH

    YLLIS J. HALL

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    2STO

    8140

    40120

    130P48643W

    6/12/1979G

    ST51

    8230

    NW

    NE

    JOH

    N D

    . & PH

    YLLIS J. HALL

    HALL #

    2STO

    8140

    40120

    130

    P92840W9/20/1993

    GST

    5183

    11N

    WS W

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    N K. M

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    #1

    STO3

    5-4

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    nU

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    P92841W9/20/1993

    GST

    5183

    11SESW

    JOH

    N K. M

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    #2

    STO5

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    nU

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    P92840W9/20/1993

    GST

    5183

    11N

    WS W

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    P92841W9/20/1993

    GST

    5183

    11SESW

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    P92840W9/20/1993

    GST

    5183

    11N

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    P92841W9/20/1993

    GST

    5183

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    P105938W5/8/1997

    GST

    5183

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    10200

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    P109499W4/9/1998

    GST

    5183

    12N

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    ER #

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    15240

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    240P109649W

    4/15/1998G

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    6240

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    6240

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    8312

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    10200

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    200

    P109499W4/9/1998

    GST

    5183

    12N

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    ER #

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    15240

    10150

    240

  • TAB

    LE 5STA

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    INEER

    'S OFFIC

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    P109649W4/15/1998

    GST

    5183

    12SESE

    L2M

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    8180

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    180P133961W

    4/12/2001G

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    8312

    SESEL5

    JACK L. / KATHER

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    6240

    10165

    240

    P103426W8/8/1996

    GST

    5183

    13N

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    RO

    N CH

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    N #

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    10260

    39210

    258

    P103440W8/5/1996

    GST

    5183

    13SW

    NE

    MICH

    AEL/LILLAIN M

    M

    ARKO

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    ARK #

    5STO

    2320

    97305

    315

    P115878W5/20/1999

    GST

    5183

    13N

    ENE

    WES G

    UY

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    Y #1

    DO

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    20416

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    nU

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    P116666W7/6/1999

    GST

    5183

    13N

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    DAVID

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    #1

    DO

    M10

    38020

    260280

    P125226W5/10/2000

    GST

    5183

    13N

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    DO

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    42040

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    P138687W9/7/2001

    GST

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    DO

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    22034

    182200

    P145005W6/6/2002

    GST

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    13N

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    OT #

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    25380

    68360

    370P21917W

    3/27/1973G

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    8313

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    1064

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    50

    P30475W7/18/1975

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    13SW

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    AEL AND

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    8165

    38135

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    P56422W4/16/1981

    GST

    5183

    13N

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    ERRY J. &

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    ILLERM

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    7315

    60300

    312

    P66097W12/12/1983

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    ILLERM

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    10240

    30225

    235P86495W

    10/30/1991G

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    8313

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    TOLM

    AN #

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    14678

    50646

    666P87246W

    3/4/1992G

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    8313

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    TOLM

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    ARK #

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    0140

    93103

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    7/17/2001G

    ST51

    8314

    NEN

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    12395

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    385P154183W

    9/2/2003G

    ST51

    8314

    NW

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    10240

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    P156929W3/9/2004

    GST

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    14N

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    10365

    176327

    345P21918W

    3/27/1973G

    ST51

    8314

    SWN

    WH

    ELEN K. R

    AUCH

    RAU

    CH #

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    OM

    6170

    16140

    148

    P32863W4/27/1976

    GST

    5183

    14N

    WS W

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    Y MAR

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    MAR

    SHALL #

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    8251

    55U

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    n

    P39402W8/1/1977

    GST

    5183

    14SW

    S WL12B5

    WILLIAM

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    DO

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    295150

    287294

    P50950W1/17/1980

    GST

    5183

    14N

    WSW

    ALBERT G

    . & CH

    YERL J.

    TOW

    NSEN

    DH

    EATHER

    #1

    DO

    M7

    235145

    225230

  • TAB

    LE 5STA

    TE ENG

    INEER

    'S OFFIC

    E WELL D

    ATA

    BA

    SE SEAR

    CH

    Perm

    it #P

    riority

    Status

    Township

    Range

    Section

    Qtrqtr

    LotsA

    pplicant

    Facility Nam

    eU

    sesY

    ld A

    ctW

    ell D

    epthStatic D

    epthM

    wbz

    TopM

    wbz

    Bottom

    P57694W7/29/1981

    GST

    5183

    14N

    WSW

    DO

    NALD

    W. M

    ILLERD

    W M

    ILLER #

    1D

    OM

    5247

    130236

    246

    P58400W10/6/1981

    GST

    5183

    14SW

    S WD

    ENN

    IS S. & BO

    NN

    IE J. EBER

    HAR

    DT

    EBERH

    ARD

    T #1

    DO

    M4

    18095

    170174

    P18099P10/4/1963

    GST