6 October 2017
DEPARTMENT OF DEFENCE, PFAS BRANCH
Preliminary Site Investigation for PFAS RAAF Base Scherger QLD (1218)
RE
PO
RT
Report Number. 1669283-003-R-Rev2
Submitted to:
Department of Defence PFAS Branch Attention: Andrew Mitchell
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Table of Contents
1.0 INTRODUCTION ........................................................................................................................................................ 1
1.1 Poly- and Perfluorinated Substances (PFAS) ............................................................................................... 1
1.2 Background................................................................................................................................................... 1
1.3 Key Findings from the Data Gap Assessment .............................................................................................. 1
1.4 Objectives ..................................................................................................................................................... 1
2.0 SCOPE OF SERVICES.............................................................................................................................................. 2
3.0 SITE DESCRIPTION .................................................................................................................................................. 4
3.1 Site Identification .......................................................................................................................................... 4
3.2 Current Site Use ........................................................................................................................................... 4
3.3 Surrounding Land Use .................................................................................................................................. 4
3.4 Review of Defence Contaminated Sites Register ......................................................................................... 4
3.5 Historical Aerial Photographs........................................................................................................................ 6
3.6 Site Inspection & Desktop Preparations ....................................................................................................... 7
3.7 Water Supply ................................................................................................................................................ 7
3.8 Other Information Sources ............................................................................................................................ 7
4.0 ENVIRONMENTAL SETTING ................................................................................................................................... 8
4.1 Climate ......................................................................................................................................................... 8
4.2 Topography................................................................................................................................................... 8
4.3 Soil and Geology .......................................................................................................................................... 8
4.3.1 Soil .......................................................................................................................................................... 8
4.3.2 Acid Sulfate Soils .................................................................................................................................... 8
4.3.3 Regional Geology.................................................................................................................................... 8
4.3.4 Local Geology ......................................................................................................................................... 9
4.4 Hydrology ..................................................................................................................................................... 9
4.4.1 Site Surface Water Drainage ................................................................................................................ 10
4.4.2 Irrigation ................................................................................................................................................ 10
4.4.3 On-property Surface Water Use ............................................................................................................ 10
4.4.4 Off-property Surface Water Use ............................................................................................................ 11
4.5 Hydrogeology.............................................................................................................................................. 11
4.5.1 Regional Hydrogeology ......................................................................................................................... 11
4.5.2 Local Hydrogeology .............................................................................................................................. 11
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4.5.2.1 Beneficial Uses of Groundwater ........................................................................................................ 11
4.5.2.2 On-site Groundwater Use .................................................................................................................. 12
4.5.2.3 Off-site Groundwater Use .................................................................................................................. 14
4.6 Ecology ....................................................................................................................................................... 14
5.0 REVIEW OF PREVIOUS INVESTIGATIONS .......................................................................................................... 16
6.0 PFAS SOURCE IDENTIFICATION .......................................................................................................................... 19
6.1 AFFF Storage ............................................................................................................................................. 19
6.2 AFFF Use ................................................................................................................................................... 19
6.3 AFFF Disposal ............................................................................................................................................ 21
6.4 Offsite Sources ........................................................................................................................................... 21
6.5 Summary of PFAS Sources ........................................................................................................................ 21
7.0 DATA QUALITY OBJECTIVES ............................................................................................................................... 22
7.1 Step 1: State the problem ........................................................................................................................... 22
7.2 Step 2: Identification of the decision or goal of the investigation................................................................. 23
7.3 Step 3: Identify the information inputs ......................................................................................................... 23
7.4 Step 4: Define the investigation boundaries ............................................................................................... 23
7.5 Step 5: Develop the analytical approach .................................................................................................... 23
7.6 Step 6: Specify performance or acceptance limits ...................................................................................... 24
7.7 Step 7: Develop the plan for obtaining data ................................................................................................ 25
8.0 SAMPLING, ANALYSIS AND QUALITY PLAN ...................................................................................................... 28
9.0 ASSESSMENT CRITERIA ....................................................................................................................................... 28
10.0 RESULTS FIELD PROGRAM ................................................................................................................................. 29
10.1 Description of Site Conditions ..................................................................................................................... 29
10.1.1 Soils ...................................................................................................................................................... 29
10.1.2 Groundwater ......................................................................................................................................... 30
10.1.3 Surface water and Sediment ................................................................................................................. 30
10.2 Data Validation ........................................................................................................................................... 31
10.2.1 Data Quality Indicators for Field Program ............................................................................................. 31
10.2.2 Data Validation Conclusion ................................................................................................................... 33
10.3 Laboratory Analysis .................................................................................................................................... 33
10.3.1 Soil Results ........................................................................................................................................... 33
10.3.2 Groundwater Results ............................................................................................................................ 34
10.3.3 Sediment and Surface Water Results ................................................................................................... 35
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10.3.4 Investigation Derived Waste ................................................................................................................. 36
11.0 CONCEPTUAL SITE MODEL ................................................................................................................................. 36
11.1 Sources ...................................................................................................................................................... 36
11.2 Migration Pathways .................................................................................................................................... 37
11.3 Exposure Pathways .................................................................................................................................... 38
11.4 Receptors ................................................................................................................................................... 38
11.5 Data Gaps .................................................................................................................................................. 40
12.0 CONCLUSIONS AND RECOMMENDATIONS ........................................................................................................ 40
12.1 Conclusions ................................................................................................................................................ 40
12.2 Recommendations ...................................................................................................................................... 40
13.0 IMPORTANT INFORMATION .................................................................................................................................. 41
14.0 REFERENCES ......................................................................................................................................................... 42
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FIGURES
Figure 1 Site Locality
Figure 2 Site Features
Figure 3A Key Map
Figures 3-1 to 3-16 Investigation Location Sub-Maps
Figure 4 PFOS in Groundwater
Figure 5 PFOS in Surface Water and Sediment
Figure 6 PFOS/PFHxS Results Overview in Groundwater
and Surface Water
Figure 7 Conceptual Site Model
TABLES
Table A Groundwater Gauging Data
Table B Groundwater Field Quality Parameters
Table C Surface Water Field Quality Parameters
Table D Groundwater Analytical Results
Table E Surface Water Analytical Results
Table F Tap Water Analytical Results
Table G Soil Analytical Results
Table H Sediment Analytical Results
Table I Investigation Derived Waste Analytical Results
APPENDICES
FIGURES
TABLES
APPENDIX A AFFF Summary
APPENDIX B Photographs
APPENDIX C Aerial photographs
APPENDIX D Topographic Map and Identified Natural Springs
APPENDIX E Registered bore search
APPENDIX F Borehole logs
APPENDIX G Data Validation
APPENDIX H Laboratory Certificates
APPENDIX I Well Survey Report
APPENDIX J Report Limitations
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DEFINITIONS AND ABBREVIATIONS
Acronym Definition
6:2 FTS 6:2 Fluorotelomer sulfonic acid
ADF Australian Defence Force
AFFF Aqueous Film Forming Foam
AHD Australian Height Datum
ALS Australian Laboratory Services
AMG Australian Map Grid
ANZECC Australian and New Zealand Environment and Conservation Council
ASC NEPM National Environment Protection (Assessment of Site Contamination) Measure
ASRIS Australian Soil Resource Information System
ASS Acid sulfate soil
B(a)P Benzo(a)pyrene
BoM Bureau of Meteorology
BTEX Benzene, toluene, ethylbenzene, xylenes and naphthalene
COC Chain of Custody
CoPC Contaminants of potential concern
CSM Conceptual site model
CSR Defence Contaminated Site Register
DCD8 Defence Contamination Directive #8
Defence Department of Defence
DNRM QLD Department of Natural Resources and Mines
DO Dissolved oxygen
DoE Department of the Environment
DP Deposited Plan
DQIs Data quality indicators
DQOs Data quality objectives
EC Electrical conductivity
EHP QLD Department of Environment & Heritage Protection
EIS Environmental Impact Statement
ESA Environmental Site Assessments
FSANZ Food Standards Australia New Zealand’s
GIL Groundwater investigation level
GIS A geographic information system
GPA General Purpose Apron
GPS Global Positioning System
HDPE high density polyethylene
LDPE low density polyethylene
LGA Local Government Area
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Acronym Definition
LNAPL Light Non-Aqueous Phase Liquid
LOR Limit of reporting
LQL Laboratory Quantitation Limits
NATA National Association of Testing Authorities
NDD Non-destructive digging
NEPC National Environment Protection Council
NEPM National Environment Protection Measure
NES National Environmental Significance
NHMRC National Health and Medical Research Council
OLA Ordnance Loading Area
PAH Polycyclic aromatic hydrocarbons
PFAS Per- and poly-fluoroalkyl substances
PFHxS Perflurohexane sulfonic acid
PFOA Perfluorooctanoic acid
PFOS Perfluorooctane sulfonate
pH A description of the acidity or alkalinity of a substance
PSI Preliminary Site Investigation
QA/QC Quality Assurance / Quality Control
RAAF Royal Australian Air Force
RPD Relative Percentage Differences
RTAW Rio Tinto Alcan Weipa
SAQP Sampling Analysis and Quality Plan
SOPs Standard Operating Procedures
STP Sewage Treatment Plant
SWL Standing Water Level
TDS Total dissolved solids
TOC Total organic carbon
TPH Total petroleum hydrocarbons
USEPA United States Environmental Protection Agency
UST Underground Storage Tank
VOC Volatile organic compounds
UNITS
Units Description
ha hectares
km kilometre
L litre
m metre
m AHD Metres Australian Height Datum
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Acronym Definition
m bgl Metres below ground level
RL Relative Level
μg/kg Micrograms per kilogram
μg/L Micrograms per litre
°C Temperature in degrees Celsius
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1.0 INTRODUCTION
The Department of Defence (Defence) engaged Golder Associates Pty Ltd (Golder) to undertake a
Preliminary Site Investigation (PSI) of the RAAF Base Scherger (Queensland), Defence property 1218. The
PSI focussed specifically on the investigation of the contaminant group per- and polyfluoroalkyl substances
(PFAS).
1.1 Poly- and Perfluorinated Substances (PFAS) Per- and polyfluoroalkyl substances (PFAS) are internationally commonly used chemicals in the production of stain repellents, lubricants, fire retardants and suppressants, including Aqueous Film Forming Foams (AFFF), and pesticides, and as industrial surfactants and emulsifiers (US EPA, 2005). AFFFs are ‘Class B’ fire-fighting foams used to prevent or extinguish flammable liquid fires. AFFF forms a barrier that inhibits oxygen from feeding the fire, while limiting volatilisation of flammable vapours from fuels.
Historically (from the 1970s), Defence used AFFF (commonly 3M LightwaterTM) that contained
perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA). From 2004, Defence commenced
phasing out legacy AFFF across the Defence Estate. The chemical structures of PFAS make them extremely
resistant to breakdown. As a result, they are persistent once released to the environment. On the basis of its
physical properties, PFOS is essentially non-volatile, and would not be expected to evaporate from water
(US EPA 2005). Infiltration of water could carry PFOS/PFOA into the subsurface or into groundwater. In soil-
water mixtures, PFOS has a strong tendency to remain in water due to its solubility.
1.2 Background
Defence has been undertaking a program of works to consider the potential for PFAS contamination relating
to the use and storage of legacy AFFF products across the Defence Estate. As part of this program, it was
identified that a PSI was required at RAAF Base Scherger to address the uncertainties associated with the
use of AFFF and the sensitivity of potential receptors. The findings from this PSI will be used by Defence to
consider the need and program priority for further detailed site investigation.
1.3 Key Findings from the Data Gap Assessment
A summary of the key findings of AFFF use from the Data Gap Assessment (Golder, 2016) were:
Fire emergency training was undertaken at the Base during an exercise in 2005, involving generation of
foam. The exact location of training could not be confirmed but was considered likely by the RAAF
personnel to be in areas aircraft occupy and operate, including taxiways and hangers. Fire trucks were
parked in Building 7 during the 2005 exercise.
Waste AFFF (until 2011) from servicing of fire extinguishers was disposed to ground at the locations
where extinguishers stored (Ordnance Loading Areas (OLAs), Hangers, General Purpose Apron (GPA)
and areas where fuel stored). From 2011 to 2014 these were centralised to OLA3, OLA8 and GPA.
Groundwater is extracted at the property for use. Likely groundwater extracted off-property.
Ephemeral streams on the property.
No known emergency use of AFFF at the property was reported by the Defence site personnel.
No monitoring results were available as part of the data gap assessment.
1.4 Objectives
The objective of the scope is to complete a PSI in accordance with the National Environment Protection
(Assessment of Site Contamination) Measure (ASC NEPM) (NEPC, 2013) including the assessment of
specific data gaps for the property and the collection of environmental samples.
The PSI is limited to use, storage and waste disposal associated with AFFF products and associated
potential PFAS contamination at the property.
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An additional objective of the PSI was to obtain information required for the proposed priority re-
categorisation with respect to the following:
Significance of AFFF use:
Confirmation of potential source areas and additional understanding of AFFF storage, use and
waste disposal.
Obtain environmental data for PFAS in soil, sediment, surface water and groundwater at or down-
gradient of identified source areas to further the understanding of the significance of AFFF use.
Sensitive Receptors:
Provide greater understanding, without external stakeholder engagement, of potential sensitive
receptors of contamination. In particular, consideration of human receptors and receptors
associated with the human food chain.
For clarity the objective of the PSI is not to assess the nature and extent of PFAS contamination (if present).
As such, the understanding of PFAS contamination at the completion of the PSI will be preliminary and there
is likely to be data gaps associated with initial Conceptual Site Model developed. Given the preliminary
nature of the investigation and the objective to collect sufficient information for re-categorisation, the
investigation was completed within the boundaries of the property and not off-property.
Given the specific objectives of the PSI the scope of services outlined does not include all aspects of a PSI
that would be undertaken if the complete contamination history was to be considered, such as title history,
searches of government/local council records etc., as these type of searches were considered unlikely to
provide additional information required to achieve the project objectives than what would be determined from
the scope undertaken. In addition, given the focus of the investigation is the historic use of AFFF and
potential PFAS contamination, no analysis of non-PFAS contaminants was included in the scope.
During the reporting timeframe of the project, Defence adjusted the scope of work to remove the re-
categorisation task as it was no longer required as part of the on-going Defence PFAS Program
development. Notwithstanding this change, the purpose of the PSI was primarily to gather additional
information to develop the understanding of the PFAS conceptual site model (CSM) and identify the issues
that may require further investigation.
2.0 SCOPE OF SERVICES
The following tasks were completed for the scope of services:
Obtain, review and consolidate existing reports and information relating to use, storage and waste
disposal of AFFF, environmental conditions (geology/hydrogeology etc.), including:
Data Gap Assessment (Golder, 2016).
Reports held on the Defence Contaminated Site Register (CSR).
Follow up interviews with Defence personnel as required (including identification of personnel not
interviewed as part of the Data Gap Assessment).
Review existing investigations reports to confirm the presence of available monitoring well locations,
either located in the immediate vicinity of potential source areas or down-gradient of potential source
areas.
Obtain and review of publically available historical information for the Property including:
Historic aerial photographs.
Topographical, soil and geological maps.
Undertake site reconnaissance to gain an understanding of the existence and use of water supply bores
in the vicinity of the property. This included review of current land use where registered bores are
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located. At this stage of the project life-cycle, this PSI did not include engagement with external
stakeholders to confirm water use. However, as part of the interviews with Defence personnel further
understanding of the use of groundwater and surface water off-property was sought.
Undertake site inspections to ground truth additional information obtained from the desktop reviews and
interviews. Provisionally select investigation locations prior to preparation of the Sampling Analysis and
Quality Plan (SAQP).
An initial Conceptual Site Model (CSM) was developed, based on the available information. The CSM
identified potential sources, possible pathways for contaminant migration and potential receptors for
PFAS contamination. Based on the initial CSM, the targeted sampling program was presented in a
SAQP (Golder 2017). The SAQP provided justification for the proposed targeting sampling locations,
media to be sampled and analytical program. The SAQP also included details on the methodologies
employed across the sampling, analytical and quality aspects of the program to ensure that the data
obtained is of a quality required for the objectives of the PSI. Field QA/QC was implemented in
accordance with NEPM procedures and particular attention paid to avoiding PFAS cross-contamination
from sampling methods or equipment. The CSM was subsequently refined based on the results of the
investigation program and presented in this PSI report.
Collection of soil samples from six soil bores and conversion into groundwater monitoring wells at the
following locations:
General Purpose Apron (BH022)
Fire Station Building 7 (BH023)
Ordnance Loading Area 3 (OLA3) (BH024)
Ordnance Loading Area 8 (OLA8) (BH025)
South-western portion of site on access road to Sewage Treatment Plant (BH026)
North-western portion of site near site boundary (BH027)
Soil samples were collected between 0.5 and 1.0 m below ground level (m bgl), and a deeper sample
targeting just above the water bearing zone to a total depth of between 7.25 m and 16.75 m.
Groundwater was sampled from four existing groundwater monitoring wells and the six new wells. The
existing monitoring wells targeted the shallowest groundwater unit at the following potential source
areas:
Aviation Fuel Farm (RAAFSGR10)
Central Power Station (RAAFSGR14)
Motor Transport Facility (RAAFSGR18, RAAFSGR19)
Water for Base water supply was sampled from the Water Treatment Plant (WTP) pre-treatment
(W002) and post-treatment (W001). Groundwater is used for water supply.
Where accessible, sampling and analysis of the identified surface water streams. This involved the
collection of 6 surface water samples. In addition, 13 sediment samples were collected from natural
and formed surface drainage features around the Base.
Samples were analysed at ALS Environmental (primary laboratory) and Eurofins MGT (secondary
laboratory), using National Association of Testing Authorities (NATA) accredited methods.
Preparation of a PSI report in accordance with the requirements of ASC NEPM (NEPC, 2013).
Updating of the Defence CSR for each property with the results of the PSI.
The site inspection and field investigation scope were completed in March and May of 2017 respectively.
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3.0 SITE DESCRIPTION
3.1 Site Identification
RAAF Base Scherger is within the Cook Shire and is located in Mission River, approximately 26 kilometres
east of Weipa in Cape York, Queensland. The Base, containing the airfield core area, is approximately
5,500 hectares (ha). The Base property lies north and south of the Peninsula Developmental Road (PDR). In
the initial Environmental Management Plan prepared by GHD for the Base (GHD, 1998), the total airfield
buffer area is about 13,000 ha which extends from Mission River in the north to Marmoss Creek in the south
(GHD, 1998).
The site location is illustrated in attached Figure 1.
3.2 Current Site Use
RAAF Base Scherger is a “bare base” staffed by limited personnel. While the base has facilities to cater for
400 personnel in fixed accommodation, 1000 personnel in tent lines, it is typically staffed by four Air Force
personnel who are responsible for caretaker duties. RAAF Base Scherger was opened in 1998.
The property contains accommodation facilities, administration buildings, fuel storage bunkers, hanger
space, munitions priming and storage, sewage treatment plant, water treatment plant and landfill. A primary
runway is approximately 3km long and associated taxiways are located in the north eastern portion of the
property.
Figure 2 provides a summary of the key features relevant to this project referenced in this report.
The land parcel reserved for the Base also includes an area south of the Peninsula Development Road as
illustrated in Figure 1. During the course of this PSI it was established with Defence personnel that Defence
use of this land was very limited (no infrastructure) and that therefore testing or servicing of fire equipment
was considered unlikely.
The features, facilities and areas of RAAF Base Scherger are presented on Figure 2.
3.3 Surrounding Land Use
Land tenure of the Weipa region is mostly Crown land subject to mining leases and pastoral leases which
are mainly cattle stations on unimproved natural pastures.
Surrounding land use includes the following:
North – The Mission River and associated flood plains, generally scrubland.
East – Ephemeral streams flowing into Mission River and scrubland.
South – The Peninsular Developmental Road. South of the Peninsula Development Road, Defence
have further land holdings south of which are bushland and streams flowing towards the Embley River.
West – Streams feeding into the Mission River and Rio Tinto’s eastern Weipa bauxite mining
operations. A residential accommodation camp occupied by the indigenous Peppin1 community is
located between the western boundary and the mining operations.
Various recreational activities occur in the region, including trail-bike riding, shooting, camping and fishing.
3.4 Review of Defence Contaminated Sites Register
The Defence Contaminated Sites Register lists five contaminated sites within the Scherger Base. The nature
of the contamination is related to hydrocarbon contamination associated with the storage of fuel and waste
oil products at the motor transport facility, central power station, aviation fuel farm, sewage treatment plant
pump shed, airfield lighting power centre and AVTUR storage facility.
1 The spelling of Peppin varies between sources and may be described as Peppin, Pappan or Peppan, This report faithfully transcribes the spelling from sources and the names should be considered interchangeable
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The CSR was last updated in 20/06/2014. There are no entries in the contaminated sites register associated
with PFAS compounds.
The primary source areas list in Table 1 which are the subject of this PSI are associated with the following
contamination issues:
Table 1: Defence Contaminated Sites Register
AFFF Suspected Source Area
Contaminated Sites Register Identification
CSR description of known issues
Motor Transport Facility
NQ0213 High Risk rating
Vehicle Refuelling point (Building 740) at the Motor Transport
Facility & Equipment Compound; Three USTs (asset codes
UST_001-UST_003) located to the north of Building 740). No
non-aqueous phase liquid (NAPL) reported. Minor hydrocarbon
concentrations below investigation levels were reported in three
of the four groundwater monitoring wells (RAAFSGR19-21).
Central Power Station
NQ0228 High Risk rating
Central Power Station – Two USTs (UST_004 and UST_005) located in front of building 800 and two ASTs (AST_006 and AST_007) located inside Building 800. No NAPL reported. Minor hydrocarbon concentrations in two wells sampled in November 2012 located immediately adjacent and to the east, inferred as down-gradient, of USTs.
Aviation Fuel Farm NQ0235
High Risk rating
AVTUR Storage Facility – bulk storage USTs (UST_011 to UST_025) containing AVTUR, waste AVTUR and waste water / AVTUR runoff from dispensing areas (UST_024-UST_025).
No NAPL reported. Elevated hydrocarbon concentrations reported in May 2009. Leak detection well sampling in 2012 indicated loss of containment to varying degrees from USTs. No hydrocarbon concentrations were detected in groundwater at RAAFSGR13 located adjacent to tank group 4 (where the highest concentrations were detected).
Sewage Treatment Plant Pump Shed Building 902 (inside)
QLD1007
High Risk rating
Sewage Treatment Plant & AST for running pump for irrigation AST is located inside Building 805.
Sewage Treatment Plant used for base operations.
1218_AST_027 (60L) Active / Diesel / Day Tank for running pump for irrigation of treated effluent. Known overflow events especially during the wet season, effluent is often disposed of via irrigation. AST containing diesel.
Airfield Lighting Power Centre Building 9
NQ0230
Medium risk rating
AST (AST_008) located inside back-up generator building 009. UST located in front of Building 009 (UST_009).
AVTUR Storage Facility - Building 427 (inside)
NQ0234
Medium risk rating
Inside building 427, adjacent to AVTUR facility. AST not located by Golder in 2012. AST_010 containing unknown product. Reported decommissioned since at least 2005 (HLA, 2005 in Golder 2013)
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3.5 Historical Aerial Photographs
Given the remote location and relatively recent mining expansion in Weipa, historical aerial photography
prior to 1988 is limited. Historical aerial imagery for 1969 was sourced from Queensland’s Department of
Natural Resources and Mines (DNRM) for review. Images from 1988 to 2002, 2005 and 2013 were observed
via Google Earth. Copies of the aerial photographs referenced above are included in Appendix C.
The aerial photograph review was conducted to establish a general history of the development of the
property and surrounding area, and to the extent possible (given photograph quality and scales) consider
fire-fighting training areas. This review is summarised in Table 2.
Table 2: Historical Aerial Photograph Review
Date Photo Reference Description of Conditions
1969
Weipa D54-3
124-151 Run 6
CAB352
Onsite: Site appears undeveloped. No roads or tracks apparent on or near the site.
Offsite: Geological survey tracks apparent to the distant west of the site in the locality of the current mining operations.
1988 Google Earth 12/1988
Onsite: Site appears undeveloped. Peninsular Development Road (PDR) established to the south.
Offsite: The PDR has been cut and constructed. Geological survey tracks and marks apparent around the PDR to the south of the site.
1990 Google Earth 12/1990
Onsite: Minor clearing onsite that matches current runway alignment and some structure locations and site tracks.
Offsite: Geological survey tracks to the south and west of the site.
1993 Google Earth 12/1993
Onsite: Further clearing on-site including the perimeter fence, administration area, accommodation camp and other areas.
Offsite: Geological survey tracks to the south and west of the site.
1996 Google Earth 12/1996
Onsite: Clearing and earthworks visible matching current site layout. Runway appears to be complete however taxiways do not.
Offsite: Geological survey tracks to the south and west of the site.
Minor clearing in the general vicinity of the Peppin community.
1999 Google Earth 12/1999
Onsite: Site was opened in 1998, site is now operational. Site appears generally consistent with recent imagery.
Offsite: Geological survey tracks to the west appear overgrown.
2005 Google Earth 12/31/2005
Onsite: No observable changes.
Offsite: Limited observable area outside of property
2013 Google Earth 9/19/2013
Onsite: No observable changes from the previous image.
Offsite: Clearing to the southwest of the site associated with mining
operations.
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3.6 Site Inspection & Desktop Preparations
An inspection of the Scherger Base and surrounding area was conducted on 7 March 2017. The following
activities were undertaken to develop an understanding of the known former uses of AFFF on the property,
and current use of surface water and groundwater both on and off site:
Interview of Defence identified personnel regarding AFFF site activities and information on water use on
and around the site. Personnel included:
Sergeant Graeme Whitaker who has been posted at RAAF Base Scherger since January 2017 and
therefore had limited knowledge on the historical usage of AFFF.
As part of the preparation for the site visit, some additional information was supplied by Warrant
Officer (WOFF) Brian Hughes. WOFF Hughes had been present at the previous site visit (June
2016) and has a longer tenure with various postings to Scherger (including being on Base during
the Exercise Kakadu in 2005).
Brief discussions were also held with Defence Contractors working on base during the time of the
inspection, including:
The representative from Lewie Fire had been working at Scherger for approximately 4 years.
The Enviropacific representative was a former Defence member until 2016 (Luke Spottiswood)
who had worked at Scherger since 2014 in the care and maintenance team.
During the site inspection, identified AFFF source areas were visited and the logistics of sampling at
each location were considered. In addition, the drainage pathways from each AFFF source area were
reviewed. The presence of Croton Hirtus, an invasive weed was also considered to design sampling
works that would not cross-contaminate parts of the property not impacted by Croton Hirtus.
3.7 Water Supply
An understanding of onsite water use was developed based on discussions with Sergeant Whittaker, the
Lewie Fire Contractor, and general observations made during the site inspection.
Bore water is extracted on Base, treated and subsequently used for a range of purposes. Until second half of
2016 treated bore water was used for onsite drinking water supply. Bore water is the current source for
domestic water supply including showers, laundry and all other on-Base purposes.
The water treatment plant is located south of the Motor Transport Facility and north-west of the
Accommodation Camp. Extraction bores supplying this plant are located in the apron surrounding the plant
and access road to plant. Four bores have been in operation at this location. Bores 1 and 2 were
decommissioned in approximately 2011 after the bore casing collapsed. Bores 3 and 4 were reported to be
still operational and were installed in approximately 2011. The Lewie Fire Contractor indicated in March
2017 that a new extraction bore is planned for installation in the water treatment plant apron area.
Additionally, it was reported that another bore was installed at the accommodation camp. The history of its
use could not be confirmed and existing site staff had no knowledge of it being operated.
Offsite indigenous camps have access to both bore and surface water as the primary water source. A
summary of on and off property surface water and groundwater use is provided in Section 4.4.3 and 4.4.4.
3.8 Other Information Sources
Other searches usually conducted as part of a PSI (for example a Certificate of Title search) were not
undertaken as it was considered that they would either contain limited beneficial information with respect to
potential AFFF use and/or would not be available for commonwealth lands, such as historical title
documents, council records or work cover documentation for storage of goods.
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4.0 ENVIRONMENTAL SETTING
Information from a number of sources, including previous site investigations and public reports on regional
information were reviewed to establish the environmental setting of the site. Knowledge of the environmental
setting provides an initial understanding of the potential PFAS migration pathways and the sensitivity of the
receiving environment.
4.1 Climate
The nearest Bureau of Meteorology (BOM) weather station is Weipa Aero (Station 027045), located
approximately 15 km south west from the Base. The site has been active since 1941. The climate statistics
outlined in this section are based on data between 1992 and 2017.
Weipa is part of Australia’s northern tropics, a climate dominated by hot, wet, monsoonal summers and dry,
relatively cool winters. Weipa Aero Station reported daily maximum average temperatures are between
31.0°C and 35.6°C year round, with annual overnight minimums averaging between 18.7°C and 24.2°C.
The Weipa area has an average annual rainfall of 1,932 mm. Rain occurs on an average of 71 days of the
year. Rainfall shows seasonal variation throughout the year, with the approximately 85% of the mean annual
rainfall in December, January, February and March. The maximum number of rain days per month is 15,
occurring in January. The lowest mean monthly rainfalls and rain days occur in July (0.3 days).The annual
evaporation is greater than the annual rainfall, indicating a water deficit in the area.
Annual average wind directions are predominantly from the south east or east in the morning, and vary from
the south east, east or west in the afternoon (BOM, 2017).
4.2 Topography
The surface elevation rises from 20 m AHD in the west, north and east of the runway to up to approximately
50 m AHD in the vicinity of the runway in the north-east of the Base. South-east of the airfield area, the
property rises up to approximately 45 m AHD towards the Peninsula Developmental Road. Further south of
the Peninsula Developmental Road, the topography rises up to an elevation of 100m AHD forming a plateau,
locally known as the Weipa Plateau.
The property is characterised by a ridge which is oriented northwest - southeast on which the 3km runway for
the Base is constructed, and undulating hills and valleys, through which ephemeral streams flow. The ridge
peaks at approximately 50 m Australian Height Datum (AHD). North, northeast, west and southwest of this
ridge are tributaries and minor gully flows that enter the tidally affected Mission River to the north. South and
southeast of the Base is the Peninsular Developmental Road.
4.3 Soil and Geology
4.3.1 Soil
The 1:250,000 map Soils of the Cape York Peninsula, Far North Queensland, indicates the surface soils are
likely to comprise deep gradational or uniform yellow massive soil with ferruginous or magnaniferous nodules
formed or laterised remnants of the Bulimba Formation.
4.3.2 Acid Sulfate Soils
On-line acid sulfate soil (ASS) mapping hosted by the Australian Soil Resource Information System (ASRIS)
was reviewed. The ASRIS mapping is based on existing data sets which have been converted to a national
classification system (ASRIS 2011). ASRIS ASS mapping indicates that there is extremely low probability of
acid sulfate soils occurring in the region.
4.3.3 Regional Geology
Regional mapping (1:500 000) indicates the Base is situated on Tertiary aged stratified units including
volcanic and metamorphic rock. The majority of the Base is indicated to be underlain duricrusted palaeosols
at the top of deep weathering profiles including ferricrete and silcrete, duricrusted old land surfaces.
Aluminous laterite may be present, including bauxite with sandy “A” horizons, deep weathered furukun
surface. Geology in the southern end of the Base is mapped as Paleocene-Oligocene Sediments of
sandstone, mudstone and conglomerates.
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4.3.4 Local Geology
Extensive drilling and geological logging has been conducted during the installation of 14 pre-existing
groundwater observation bores across the property and six additional wells installed for this investigation. (A
summary of groundwater observation bores at the Base is provided in Section 4.5.2.2).
Bore logs show the surface soils form of a horizon of ferricrete, described as sandy clayey gravel, silty clay
or silty sand. These shallow horizon is cemented with bauxite nodules increasing to gravels to
approximately 1.2 m depth, forming a resistant duricrust. The area around the runway is expected to be
underlain by fill material.
Underlying the ferricrete is sand of the Bulimba Formation, with intermittent bands of clayey sand, clayey
gravelly sand and silty sand, varying to sandy clays in some parts of the Base. White sand and kaolin clay
clasts are present at various depths across the Base: from 19 m depth at BH022 at GPA, and with red
mottling at BH023 from 13.5 m at Building 7 and from 10 m in the lower valley on western boundary at
BH027.
Registered bores in the vicinity installed for Comalco (now Rio Tinto) indicate the second layer of sand of the
Bulimba Formation is 5 to 8 m thick and extends to 25 m in places (Refer to registered bore records in
Appendix E). GHD (1989) found in some cases the sandy aquifer was not present rather, sandy clay only.
The onsite geology is broadly summarised in Table 3.
Table 3: Local Geology
Geological unit Depth range Description
Silty Sand
(ferricrete)
0 to 0.5 m Red brown, trace rootlets, fine to medium sand, sub-angular gravels
Clayey Gravelly Sand
(ferricrete)
0.5 to 3.5 m Fine to medium grained sand , sub-rounded bauxite gravels, brown with dark mottling
Silty Sandy Clay 1 to 6 m Orange – brown, fine to medium grained, low – medium plasticity
Silty Clay 7 to 12 m Medium- high plasticity, pale brown mottled with white kaolin clasts, grading to white kaolin
Clayey Sand 7 to 13 m White, fine to medium grained
Sandy Clay 9 to 13 m variegated with trace yellow, granular to medium-grained, quartz grains
Clay 13.5 to 19 m white, clayey with a trace of sand
Clay 17 to 22.5 m Brown with some white and yellow mottling, grading to t white with red and yellow mottling some fine sand, high plasticity
4.4 Hydrology
There are several surface water features associated with the property area. The Base EMP (GHD, 1998)
describes six spring sites of significance to Aboriginal people with interest in the land are located on and in
close proximity to the Base (GHD, 1998).
The locations of the springs have been identified in prior reporting (GHD, 2002):
Springs 1, 2, 4 and 6 are located within the Base fence line
Spring no. 5 is located just outside the south-western boundary fence
Spring no. 3 was not mapped.
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The Mission River is located approximately 4.5 km north and a number of the natural springs onsite flow into
ephemeral tributaries and gullies that feed into this river (QLD Globe, 2017).
In a report documenting the outcomes of environmental monitoring for EMP compliance in 2001, GHD
reported that regular monitoring of groundwater bores installed throughout the Base in 1988 indicates that
the aquifer responds rapidly to local rainfall. Discharges occur naturally at springs and in watercourses
within the airfield buffer area boundary. (GHD, 2001).
Minor streams flowing at the southern extent of the Base (south of the PDR) drain to the Embley River
located approximately 2.4 km south west of the site. These flows are as indicated on Figure 2.
Drainage onsite is dominated by large engineered drainage channels that drain much of the hardstand area
on the south western watershed. This drainage is focused into a retention basin, before it’s discharged into
the southwestern tributaries of the Mission River. The water within the drainage lines on-site is not known to
be collected or used for any purposes such as irrigation or stock watering.
Salinity of the regional watercourses (Gulf Rivers zone) have been described in the Queensland Water
Quality Guidelines (QLD DEHP, 2013) as a moderate salinity zone.
4.4.1 Site Surface Water Drainage
The formed drainage network at the Base generally runs in a north-south direction and later meets tributaries
of the Mission River. The Mission River is a large water body which flows westerly discharging into the Gulf
of Carpentaria.
The formed drainage network generally follows the natural topography. Appendix D provides a detailed
topographic map of RAAF Base Scherger (GHD, 2001) with the location of natural springs.
Drainage generally associated with the key AFFF source areas (Section 6.0) flows in southerly direction and
the drainage channels join and discharge to a retention basin (asset reference 409), located centrally onsite,
immediately south of the main site access road. Releases from the retention basin are directed in a south to
south-easterly direction (refer topographic and drainage map, Appendix D) entering a tributary of the
Mission River.
Due to the extensive wet season in Cape York, the drainage channels and retention pond have been
designed and constructed for significant volumes of water and are of an earthen construction (unsealed).
The retention pond has been designed to settle water and then allow a more controlled release of water.
This is likely to result in the retention pond being a depositional environment for any sediments (and
associated contaminants bound to the sediments) moving in the stormwater.
Historically, a small dam (known as “Blue Lagoon) was constructed onsite for use in the construction of the
Base (prior to 1998) for water supply for dust suppression. The dam was subsequently drained and no
longer used as a permanent water storage body.
4.4.2 Irrigation
The property contains a number of irrigated areas including the gardens and grassed areas at the residential
homes on Base, the dog yards and the accommodation camp on the Base.
Based on the discussions held with base management, it is understood that irrigation water is sourced from
treated bore water extracted and treated on site at the water treatment plant located in the southern portion
of the Base (refer Figure 2).
4.4.3 On-property Surface Water Use
There is no use of water from the on-property surface water drainage lines.
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4.4.4 Off-property Surface Water Use
Peppin Elders provided WOFF Hughes with information about the current water supply at the Peppin
Indigenous Camp in early 2017. It was understood from the Elders that the camp has not been used
recently as the septic sewage system has been backing up. When the camp is in use, bottled water or
surface water from the nearby creek is collected for water supply.
The extent of recreational activities on the Mission River for recreational activities (either water sports or
fishing) is not confirmed.
4.5 Hydrogeology
4.5.1 Regional Hydrogeology
The baseline hydrogeological study completed in advance of the Base construction provided a foundation
study of the groundwater resources in the locality of the property (GHD, 1989).
Key findings from this study (which have been reiterated in subsequent reports prepared by GHD) included:
The groundwater resources of the Bulimba Formation have been used extensively for the supply of both
industrial and domestic water to the mining operations and Weipa town.
The principal shallow aquifer used is the sandy horizon 3 m to 14 m thick which occurs approximately
6 m to 13 m below ground surface.
The principal shallow aquifer is considered to be an unconfined horizontal aquifer system which is
recharged annually by downward infiltration into the bauxite zones overlying the sandy member (GHD,
1989). This finding was corroborated by Maunsell (2005) with the identification of bauxite / ferricrete
from ground surface to approximately 5 m or 6 m depth, underlain by the shallow sand aquifer to
approximate depths of 11 or 12 m.
An additional deep aquifer is present in the underlying Garraway Beds at a depth of about 900 m where it
forms a confined artesian source (GHD, 1989).
4.5.2 Local Hydrogeology
Local hydrogeology varies according to local topography and season (wet or dry). Water is expected to flow
away from the ridgeline on site which extends from the PDR approximately 3km into the Base at the eastern
side and approximately 1.5 km into the Base from the western side (QLD Globe, 2017).
Localised groundwater flow is also expected to be influenced by the natural springs on the Base, depending
on proximity to these springs and flow in the springs.
Feasibility studies undertaken by GHD (1998) identified that ‘the vertical recharge and local discharge from
the aquifer at the Base will ensure that use of the water for airfield purposes will not affect Weipa's supply’.
GHD (1998) identified that groundwater flow direction within the upper aquifer was considered to be towards
the west, with a calculated groundwater flow rate (permeability or k value) for the shallow aquifer estimated
at approximately 30 m/day, confirmed by Maunsell in 2005.
The local hydrogeology is broadly defined by the unconfined sands of the Bulimba Formation. In parts the
sands are replaced with sandy clays, which will retard the recharge in those locations.
4.5.2.1 Beneficial Uses of Groundwater
In Queensland, water quality guidelines are developed under the frameworks outlined in the Australian and
New Zealand Fresh and Marine Water Quality Guidelines (ANZECC and ARMCANZ 2000) which have been
prepared as part of Australia’s National Water Quality Management Strategy (NWQMS).
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Environmental values (‘EVs’) recognised in the national guidelines include:
aquatic ecosystems
primary industries, (including irrigation, stock watering, aquaculture, human consumers of aquatic
foods, general farm use)
recreational use (swimming, boating, visual recreation)
drinking water supply
industrial water
cultural and spiritual values.
4.5.2.2 On-site Groundwater Use
Given the property is Commonwealth land, a search for registered uses of groundwater in the Queensland
State databases does not necessarily provide a good indication of the presence of groundwater users.
Based on the site inspection and interview of Defence personnel, it was confirmed that groundwater is
extracted for use on the property for domestic, irrigation and other site operational purposes. Since late
2016, domestic purposes has not included drinking water supply as the Defence personnel currently use
bottled water for drinking.
A search of DNRM records in June 2017 identified seven registered groundwater bores on the Base. A summary of the information available from the DNRM bore search for these registered bore is provided in Table 4. The location of these registered bores is indicated on the map included with the bore search in Appendix E. Table 4: Registered Groundwater Bores onsite (DNRM, June 2017)
Bore ID Date
Constructed Total Depth
(m bgl)
Standing Water Level (SWL)
(m btoc)
Salinity
(µS/cm)
Comments
RN92284 1970 10.41 Not
stated Not given
Noted as “Comalco No22” on DNRM bore record
RN92285 1970 13 Not
stated Not given
Noted as “Comalco No23” on DNRM bore record
RN78994 Not stated Not stated 5 - 10 Not given
Original bore number noted as “Bore No. 3” on DNRM bore record.
Surveyed by RAAF in 1992.
Likely to be BH04 (GHD, 2001)
RN78995 Not stated Not stated 4 - 9 Not given
Original bore number noted as “Bore No. 4” on DNRM bore record.
Surveyed by RAAF in 1992.
Likely to be BH34 (GHD, 2001)
RN78862 1993 Not stated 5 - 10 92 Titled “Bore 1” on DNRM bore record. Located near Accommodation Camp.
RN78863 1993 Not stated 5 - 10 Not given Titled “Bore 2” on DNRM bore record. Located near Accommodation Camp
RN109173 1999 30 6.3 Not given
Titled “Peppin” on DNRM bore record. Identified in the SAQP bore search as located at the (intermittently occupied) Peppin residential camp area, 200m off-site. The current search places the bore with the Base land parcel.
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The inferred use of these 7 bores is as follows:
Two of the bores identified during the bore search were reported by GHD (2001) to be BH04 (RN78994)
and BH34 (RN78995), understood to be observation bores installed to monitor the performance of the
sewage treatment plant (up and down-gradient of the STP).
Two bores installed in 1993 are located near the Accommodation Camp and titled “Bore 1” (RN78862)
and “Bore 2” (RN78863). Defence personnel interviewed during the site inspection indicated these
bores may have been installed for potential water supply purposes, however there was no knowledge of
their use and operation.
Two further wells are registered as installed on-Base in 1970, noted as Comalco No22” on the DNRM
bore construction record (RN92284, near western boundary) and “Comalco No23” on the DNRM bore
construction record (RN92285, east of the Accommodation Camp). Purpose of these bores is not
known. Given their installation by the former mining operator (Comalco), it is inferred they were installed
for exploration reasons.
The registered location for registered bore RN109173 is located at the southern western boundary of
the Base. The position of this bore matches the inferred location of the Peppin indigenous camp which
is intermittently occupied. The DNRM record confirms it is registered to “Peppin” and was installed in
1999. The bore construction record indicates the depth of the bore is 30 m with two slotted casing
intervals (4 to 8m and then 24 to 30m). The standing water level recorded on the bore construction card
was 6.3 metres below ground level. This bore was identified in the SAQP bore search as located at the
(intermittently occupied) Peppin residential camp area, 200m off-site. The current search of the NRM
records indicated that the registered location is within the Base land parcel.
A review of previous environmental site assessment reports indicates the presence of 14 groundwater
observation bores (monitoring wells) prior to the current investigation. A summary of the pre-existing
monitoring wells is provided in Table 6.
Table 5: Groundwater monitoring wells installed on-site
Bore ID Comments / Alternative names
BH04 Reportedly installed 1988. Also referred to at RAAFSCH04, Bore No. 3, or RAAFSGR04
BH34 Reportedly installed 1988. Also referred to as Bore No. 4, or RAAFSCH_GW34
RAAFSGR10 Installed by Maunsell in 2005 (noted as RAAFSCH_GW10 (Jacobs, 2016))
RAAFSGR11 Installed by Maunsell in 2005
RAAFSGR12 Installed by Maunsell in 2005 (noted as RAAFSCH_GW12 (Jacobs, 2016))
RAAFSGR13 Installed by Maunsell in 2005 (noted asRAAFSCH_GW13 (Jacobs, 2016))
RAAFSGR14 Installed by Golder in 2013
RAAFSGR15 Installed by Golder in 2013
RAAFSGR16 Installed by Golder in 2013
RAAFSGR17 Installed by Golder in 2013
RAAFSGR18 Installed by Golder in 2013
RAAFSGR19 Installed by Golder in 2013
RAAFSGR20 Installed by Golder in 2013
RAAFSGR21 Installed by Golder in 2013
The groundwater monitoring bore network has been installed throughout a series of investigations
undertaken at the property to assess contamination. The distribution of monitoring wells reflect the objectives
of prior investigations that have been undertaken to assess the conventional contamination sources
(petroleum storage) and therefore have not specifically targeted AFFF activity. However there is some
degree of overlap with the known conventional contamination and AFFF sources.
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Groundwater monitoring well depths were from 4.9 metres below top of casing (mbTOC) to 14.2 mbTOC,
and targeted the water bearing sands of the Bulimba Formation.
4.5.2.3 Off-site Groundwater Use
A review of registered groundwater bores registered with DNRM in QLD in the vicinity of the property was
undertaken to provide additional information on groundwater use. A search of the DNRM Groundwater
Database in June 2017 indicated approximately 22 registered groundwater bores located within 2 km of the
Base. The results of the Groundwater Bore Search are displayed in Appendix E. Details are provided in
Table 6.
Table 6: Registered Groundwater Bores within 2km of RAAF Base Scherger
Bore ID Location
99245 Offsite: 2.0 km west of the property.
(located within the mining lease and described as an observation bore drilled by Comalco in DNRM record)
RN45271 Offsite: 2.0 km west of the property.
(located within the mining lease and described as an observation bore drilled by Comalco in DNRM record)
92282, 92283 Offsite: 1.3 km west of the property (located within the mining lease)
99253 Offsite: 1.7 km west of the property (located within the mining lease)
92281
99254
Offsite: 2.0 km west of the property (located within the mining lease)
157561, 157562, 157566, 157558, 157559, 157568, 157569, 157560, 157576, 157565, 157563, 157564, 157556, 157557, 92286 (15 bores)
Offsite: located south of the Peninsula Developmental Road.
The use of the water was not generally reported in the DNRM database records. Given the nature of the
surrounding land-use, a site reconnaissance was not possible to infer information on off-site groundwater
use and therefore the use of the offsite bores could not be confirmed without offsite community engagement.
The inferred use of these bores is as follows:
A number of bores are located west of the Base within the mining areas operated by Rio Tinto.
Although the location was registered with DNRM, detailed records for the construction or use of these
wells was not available in the DNRM registered bore database.
A number of bores are located south-east of Scherger (15 bores), south of the Peninsula Development
Road. The registered owner of all of these bores is not noted on the bore construction cards with the
exception of one bore (RN92286) registered to Comalco (now Rio Tinto) and drilled in 1970. The other
14 bores were drilled in 2014 and bore construction details recorded. The use of these bores could not
be confirmed from the records and interview information available.
Off-site use of groundwater for drinking water cannot be discounted given the lack of reticulated water supply
in the region. For example at the Peppin camp and possibly at the mining operations. Other use of
groundwater off-site is expected to include industrial water supply (for the mining operations) and
environmental monitoring at the mine site to the west.
4.6 Ecology
Custom environmental reports were produced for the site using the online report generator on the QLD
DEHP website. The reports requested comprised:
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Matters of state environmental significance (MSES)
Regional ecosystems
Terrestrial biodiversity and aquatic conservation values
Copies of the reports are presented in Appendix D. These reports provide information on statutory and non-
statutory environmental interests and have been used to identify potential sensitive environmental receptors.
The vegetation at RAAF Base Scherger is predominantly eucalyptus woodland and open forest of the Cape
York Bioregion and Weipa Plateau Sub region, Embley catchment.
MSES: Vegetation Management Wetlands and watercourse are mapped as present
Biodiversity and conservation values reported by EHP include:
Aquatic conservation assessment (non-riverine) is low in the centre of the Base which relates to the
isolated lacustrine waterbodies identified.
Aquatic conservation assessment (riverine) ranges from ‘very high’ in the north east and south of the
Base, to ‘high’ in the south east and ‘low’ in the north west.
Spring-fed riverine wetlands are identified as a special feature and contain plant species of
conservation significance, regional ecosystems of conservation significance and have ecological
function including refugial areas, critical habitat for plants and key resources for birds, frogs and
reptiles.
Regional ecosystems indicated to be present on the EHP mapping comprise:
Biodiversity status of remnant regional ecosystems are of no concern at present
Isolated palustrine wetlands (swamps / lakes) and lacustrine and riverine waterbodies are present in
parts of the Base
High numbers of endemic plant species are reported. The vulnerable species Gardenia psidioides, and
near threatened species Acacia fleckeri, Archidendron hirsutum, Chrysophyllum roxburghii, Croton
brachypus and Litsea macrophylla occur in this ecosystem.
Important wildlife corridor for closed forest species.
Woodlands and open woodlands dominated by ironbarks such Eucalyptus cullenii (Cullen's ironbark),
E. staigeriana (lemon-scented ironbark) or E. melanophloia (silver-leaved ironbark) and bloodwoods
such as Corymbia stockeri subsp. peninsularis, C. clarksoniana (grey bloodwood) or C. leichhardtii
(rustyjacket).
The near threatened species Acacia ommatosperma occurs in this ecosystem.
A comprehensive ecological baseline survey was undertaken at the Base by GHD and summarised within
the Environmental Management Plan prepared for the Base (GHD, 1998). The EMP reported several
variants of Darwin Stringybark (E. tetradonta) and Melville Island Bloodwood (E. nesophila) have been
described in the area. This is the most extensive form of vegetation in the Weipa district and is widely
represented on Cape York regional mapping (QLD Globe, 2017). There are no endangered flora species
recorded on the site although two species, pitcher plant (Nepenthese mirabilis) and a fern (Lindsaea walkeri)
are described as rare. They are located near to the permanent springs and their outflows.
GHD identified a total of eighteen native and three introduced (feral cats, feral pigs and cattle) animal
species that are expected to inhabit the Base. The EMP identified that streams running from the springs are
sources of drinking water for these animals, as well as for a number of birds and frogs. The only species of
freshwater fish recorded in the streams draining the Base is the rainbow fish (Pseudomugi gertrudae) which
GHD found is described as rare by the Australian Society for Fish Biology. However, GHD considered this
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may be due to the limited applicability in the far north of Australia because of the lack of information on the
region. (GHD, 1998).
Invasive weed Croton Hirtus is known to be present in parts of the Base.
5.0 REVIEW OF PREVIOUS INVESTIGATIONS
The following reports obtained from the Defence CSR were reviewed to identify potential indicators of former
AFFF use, any areas of identified PFAS contamination and to confirm the environmental setting.
Table 7: Documents Reviewed.
Author Year Title
GHD 1989 Australian Construction Services, Cape York Airfield Environmental Assessment Phase, Report on Groundwater Investigation, Report WS1, March 1989
GHD 1998 RAAF Base Scherger Environmental Management Plan
GHD 2001 Environmental Works, North Queensland, Technical Report on RAAF Scherger Environmental Monitoring
Maunsell/AECOM 2005
NQ01150 – Groundwater Monitoring Well Installation, Sample Capture
and Monitoring Report, RAAF Base Scherger AVTUR Fuel Farm
(2004/2005)
ENSR/AECOM 2009 RAAF Base Scherger Environmental Monitoring Program for Water
Quality (NQ1998)
Golder 2013 Environmental Investigation of USTs/ASTs Across the Defence Estate, Stage 1 & 2 Report – RAAF Base Scherger
Golder 2016 PFAS Environmental Management Program: Category 2 Property Data Gap Assessment – RAAF Base Scherger
Jacobs 2016 RAAF Scherger Groundwater Monitoring Report, Post Dry Season
Jacobs 2016 RAAF Scherger Groundwater Monitoring Report, Post Wet Season
Jacobs 2016 RAAF Scherger Surface Water Monitoring Report
Reports and additional information were sourced from the Defence CSR or Defence personnel. The review
focused on reports and information that included reference to AFFF use, storage and waste disposal,
historical monitoring data or environmental conditions (geology/hydrogeology etc.) at the property. This is not
a summary of all previous reports, but of only information relevant to this PFAS PSI.
A summary of pertinent documents is provided below:
1989 –Report on Groundwater Investigation, Cape York Airfield Environmental Assessment Phase
(reference 0901g, Report WS1 March 1989, GHD)
This is the earliest report available to Golder as part of this PSI on the baseline groundwater investigations at
Scherger. An exploratory hydrogeological assessment was undertaken at the proposed airfield site as part
of the initial impact assessment studies. A network of observation bores were drilled to understand seasonal
water variations, the aquifer recharge capability and the potential water supply was assessed through
installation of a production bore.
1998 –Environmental Management Plan, RAAF Base Scherger (1998, GHD)
The EMP was prepared for the operation of the Base, to provide requirements for the environmental
management of the Base and its surrounds. It contains a set of procedures for the environmental
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management of the Base, together with specific monitoring requirements and mitigation measures aimed at
minimising adverse impacts.
2001 – Environmental Works, North Queensland, Technical Report on RAAF Scherger Environmental
Monitoring (reference 42\10211\00- 46073, September 2001, GHD)
By 2001, monitoring wells BH34 (near the sewage treatment plant) and BH4 (south of the Motor Transport
Facility) had been installed and were subject to periodic monitoring. The report stated that the 2 wells were
intended for the assessment of groundwater impacts from the sewage treatment plant with BH4 upstream
and BH34 downstream.
The report also references earlier investigations by GHD between 1989 and 1992 to identify a viable
groundwater source for RAAF Scherger. It was reported that the identified aquifer at Scherger is the same
shallow aquifer (lying immediately below the bauxite) that the township and the mining operations extract
water supplies from. Water levels were reported to fluctuate over at least 2m on average between the wet
and dry seasons in the timeframe 1992 to 2001.
2005 – NQ01150 – Groundwater Monitoring Well Installation, Sample Capture and Monitoring Report,
RAAF Base Scherger AVTUR Fuel Farm (2004/2005) (reference 80200705, August 2005,
Maunsell/AECOM)
A summary of the regional geology and hydrogeology reported by Maunsell is included below:
Site geology encountered during the advancement of the groundwater monitoring wells consisted of
bauxite/ferricrete with an approximate thickness of between 5 – 6m, underlain by a shallow sand
aquifer, which reaches depths of 11 – 12m below ground level (bgl). The sand aquifer was underlain by
kaolinite clay overlaying mudstone. Maunsell installed monitoring wells RAAFSGR10 to RAAFSGR13
inclusive surrounding the Aviation Fuel Farm in 2005;
The principal aquifer used for water supply within the Base, is an unconfined sandy horizon
approximately 3 – 14m thick;
Groundwater flow direction within the upper aquifer was reported by Maunsell to be towards the west;
The calculated groundwater flow rate (permeability or k value) for the upper sand aquifer is
approximately 30 m/day
2009 - RAAF Base Scherger Environmental Monitoring Program for Water Quality (NQ1998) – Draft,
May 2009 (ENSR – AECOM)
A draft version of the RAAF Base Scherger Environmental Monitoring Program for water quality dated 2009
has been reviewed. This Environmental Monitoring Program is specific to water quality monitoring, and
builds on the outcomes of past programs and outlines the process for environmental performance monitoring
– schedule, procedures and water quality objectives. This version is superseded by the AECOM 2010 EMP
described below.
2010 - RAAF Base Scherger Environmental Monitoring Program for Water Quality (NQ1998) – Draft,
May 2009 (AECOM)
A revision of the Environmental Monitoring Program dated 2010 (AECOM) has been prepared for the Base.
While not stored on the CSR directly, it was attached to the Jacobs 2016 monitoring report as Appendix F.
This revision of the Environmental Monitoring Program sets out a sampling plan of surface waters and
groundwaters for the purpose of environmental compliance.
Surface water sample locations noted in the Program were as follows:
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RAAFSCHSW1: reference site described as In spring fed creek above junction with branch on which
RAAFSCHSW2 is located, but below springs (spring and surrounds are culturally significant and should
be avoided)
RAAFSCHSW2 (monitoring potential impacts from fuel farm): On spring fed creek closest to the fuel farm,
above the junction with the creek on which the reference Site is located.
RAAFSCHSW3 (monitoring impacts from sewage treatment plant and cumulative water impacts from
upstream sources): On spring fed creek adjacent to sewage treatment plant, downstream of potential lagoon
overflows.
Groundwater locations noted in the Program comprise: RAAFSGR_GW04 (or BH04), RAAFSGR_GW10,
RAAFSGR_GW11, RAAFSGR_GW12, RAAFSGR_GW13, RAAFSGR_GW34 (or BH34).
2013 – Environmental Investigation of USTs/ASTs Across the Defence Estate, Stage 1 & 2 Report –
RAAF Base Scherger (May 2013, Golder)
Golder completed a Stage 1 & 2 Environmental Investigation to assess potential ground contamination
associated with fuel storage across the base. The Stage 2 investigation scope included drilling of additional
groundwater wells onsite and sampling of monitoring wells specific to fuel storage areas.
Golder installed an additional six wells (RAAFSGR14-RAAFSGR19) as part of the UST/AST investigation.
Primarily these were installed around fuel storage/distribution areas.
2016 – PFAS Environmental Management Program: Category 2 Property Data Gap Assessment –
RAAF Base Scherger (September 2016, Golder)
Golder (2016) completed a Data Gap Assessment which included a desktop review and site interviews to
address information uncertainties to categorise and prioritise the investigation of the property within
Defence’s PFAS Environmental Management Program. No intrusive investigation was undertaken.
The report identified limited AFFF use (refer Section 6.2 for details). It was identified as part of the June
2016 site visit that the Base extracted groundwater for water supply requirements (including drinking water
supply). It was also indicated in June 2016 that the nearby indigenous community (Peppin) may be using
extracted groundwater for domestic water supply. Updates on this information have been received in early
March 2017 by Defence and summarised in Section 4.5.2.3. Conclusions from this Data Gap Assessment
resulted in the completion of this PSI.
2016 – RAAF Base Scherger Groundwater Monitoring Reports Post Dry Season (Round 1) and Post
Wet Season (Round 2) (September 2016, Jacobs)
The groundwater monitoring program scope was related to monitoring of fuelling operations between 2015
and 2016. Jacobs noted in their results a report from GHD in 2002 (‘Report on RAAF Base Scherger
Groundwater Monitoring’) that indicated the presence of MBAS in results from 1996 and 1997.
Methylene Blue Active Substances (MBAS) is an indicator of anionic surfactants such as detergents and as
an indicator of PFAS before specific analytical methods were available to market. Jacobs noted that anionic
surfactants were reported in the 2002 GHD report at 0.02 mg/L (20 µg/L) at RAAFSCH_GW04 (also
identified as BH04, GHD 2001) and RAAFSCH_34 (also identified as BH34, GHD2001) in their historic
results data table. Anionic substances detected by MBAS assays include sulfonates, phosphates, sulfates
and carboxylates, and given the broad nature of this test may detect naturally occurring compounds.
This assessment compared water quality concentrations to the ANZECC freshwater trigger values (95%
protection) following the framework outlined in the RAAF Scherger Environmental Management Plan (EMP)
(AECOM, 2010).
2016 – RAAF Scherger Surface Water Monitoring Report (September 2016, Jacobs)
Jacobs completed periodic surface water monitoring of three sampling sites on RAAF Scherger including
one reference site and two monitoring sites. RAAFSCHSW1 was collected close to the location of Spring
no. 1 (refer Figure 2). RAAFSCHSW2 was collected downstream of the confluence of streams arising from
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Spring 1 and Spring 2 (Refer Figure 2 for the location of Springs). RAAFSCHSW3 was collected
downstream of RAAFSCHSW2, northwest of the sewage treatment plant. Background information on the
hydrogeological and hydrological interactions between surface and groundwater was not documented in this
report.
This assessment compared water quality concentrations to the ANZECC freshwater trigger values (95%
protection) following the framework outlined in the RAAF Scherger EMP (AECOM, 2010).
6.0 PFAS SOURCE IDENTIFICATION
Presented below is a summary of the collective understanding of AFFF storage, use and waste disposal for
the property established during this PSI and the Data Gap Assessment (Golder, 2016). A summary for each
source area is presented in Appendix A.
The current Scherger Defence personnel supplemented information gathered during the 2016 Data Gap
Assessment. Given that there have been limited activations of the Base (Exercise Kakadu is the only full
Base activation in 2005), AFFF has not been used in routine training (either fire-fighting training or
equipment training) activities. AFFF has been stored in preparedness for military activation of the Base.
6.1 AFFF Storage
Identified AFFF storage included the following:
The main AFFF product historically used at the property was 3M Lightwater which contained PFOS,
PFOA and 6:2 FTS. The 3M Lightwater product was since replaced by Ansulite.
AFFF was stored in mobile equipment including fire trucks utilised during the 2005 exercise. It is
understood that a fire truck with foam capability was stored at RAAF Scherger prior to and after the
2005 exercise in Building 707.
At the time of Base commissioning, it was intended that there would be 1 x 50 litre foam fire
extinguisher at each of the following locations, totalling 15 extinguishers: OLAs (10), Marine Hangers
(2) and the General Purpose Apron (3). Subsequent to the Base being commissioned, extinguishers
were later stored in centralised locations at OLA 3 and OLA 8 for all 15 x 50 L mobile extinguishers. The
time frame for when fire extinguishers became centrally located could not be ascertained.
6.2 AFFF Use
AFFF was used in a training exercise for emergency fire response or discharged to ground during
extinguisher maintenance. Further details of AFFF use at Scherger Base has been summarised in Table 8.
Table 8: Potential AFFF use
AFFF Use Area Frequency Use Description
2005 Exercise Training Areas (unknown locations)
Fire trucks parked at Building 7 fire station during the exercise.
one-off for 2005 Exercise
Building 7 is the nominated fire station for RAAF Base
Scherger. During the 2005 Kakadu Exercise, fire trucks were
stationed here. During the course of this investigation,
Defence were not able to identify personnel who had first-
hand knowledge of the extent of training that was undertaken
during the 2005 Kakadu Exercise.
Defence personnel indicated as part of air movements that
would have occurred during the Exercise, that testing of the
fire equipment would have included the generation of foam.
However, the location where the fire equipment was tested
could not be confirmed by Defence personnel interviewed.
Noting that no firsthand knowledge was available, Defence
RAAF personnel suggested that foam training may have been
undertaken at a range of locations including the roadways
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AFFF Use Area Frequency Use Description
immediately adjacent to the Fire Station and the helipad
opposite, the taxiway, the OLAs, GPA and runway based on
their aviation exercise experience.
Building 7 is located approximately 150 m from the taxiway.
Immediately opposite and east of Building 7 is a large open
piece of cleared land comprising two helipads with an access
road to the helipads.
In the absence of firm knowledge of the exact locations for
fire training, it would seem plausible, to the current Defence
personnel, that fire training may have occurred in this locality
given the nearby presence of the fire station and that foam
training near the taxiway may have been restricted due to
aircraft movements during the Exercise. Additionally, the
taxiway is over 3km long and any fire training on the taxiway
may have occurred at discrete unidentified locations along its
length making the targeted selection of investigation locations
not possible.
OLAs and Marine Hangers
Annually between 1998 and 2014
Extinguishers were positioned at OLAs and Marine Hangers
for Base preparedness in case of fire emergency. Fire
extinguishers were serviced annually and involved purging of
the waste AFFF onto the ground at each storage location until
approximately 2014.
It was reported that early in the Base’s operation, that the
storage location of extinguishers was relocated to both OLA3
and OLA8 for ease of access when servicing.
The exact location of the extinguisher servicing and disposal
of waste AFFF at the OLA3 and OLA8 was not known.
Surface drainage from the OLA areas flows via formed
drainage channels ultimately to the retention basin (see
discussion below).
The site personnel were not aware of fire incidents or fire
training using the extinguishers.
General Purpose Apron
Annually until 2014
At the GPA it is understood that maintenance of fire
extinguishers containing AFFF involved discharging the
contents of the extinguisher to ground. This practice is
understood to have occurred until circa 2014. Site personnel
observed this occurring on the northern side of the Air
Movements Hanger (asset reference 001). Site
observations and review of site drawings confirmed that the
drainage in this locality flows both locally to the south-east
(from the eastern side of the facility) and secondly, a major
component of the flow discharges to the south-western side
of the GPA towards an oil-water interceptor. The component
of the drainage associated with observations of AFFF
disposal is locally towards the south-east. Subsequently, the
drainage from both of these areas ultimately drains to the
retention basin (see discussion below).
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AFFF Use Area Frequency Use Description
The site personnel were not aware of fire incidents or fire training using the extinguishers.
Building 707 Warehouse
Annually from 2014
Since 2014, Lewie Fire has used this warehouse for the servicing of their contracted fire extinguishers. Fire extinguishers are serviced annually and involve purging of the waste AFFF into IBC. Alternately, waste extinguishers are removed offsite and replaced with new extinguishers. Previously foam fire truck parked in this warehouse.
Motor Transport Facility (Vehicle Refuelling) - Building 701; and
Aviation Fuel Farm; and
Fuel Tanker Refuelling Bay
Annually Extinguishers positioned at each of these facilities for Base preparedness in case of fire emergency. Serviced centrally in Warehouse 707 or alternately old extinguishers replaced with new.
The Aviation Fuel Farm is topographically downgradient of the OLAs
Motor Transport Facility
Once off observation of AFFF waste disposal
Information received during the 2017 site inspection from a
Lewie Fire Contractor included a report of possible historical
discharge of waste AFFF to ground in this vicinity. The
observation made was a once off rather than knowledge of an
ongoing routine waste disposal practise. It’s understood that
the possible waste disposal occurred on the northern end of
the motor transport facility compound.
6.3 AFFF Disposal
Based on the interviews conducted with Defence personnel, there were no known major spills or leaks of
AFFF concentrate at the property.
From approximately 2014, waste disposal practises of AFFF during extinguisher maintenance was changed.
Waste AFFF was temporarily stored onsite in IBC. IBC consequently transported offsite for appropriate
disposal by Chubb.
Alternately, waste extinguishers are removed offsite and replaced with new extinguishers.
6.4 Offsite Sources
Mining operations occur to the immediate west of RAAF Scherger. The extent of fire protection equipment
(or its disposal) or if any fire response training is conducted at the mine could not be established as part of
this scope.
6.5 Summary of PFAS Sources
Based on the information reviewed and reported by Defence, the most likely sources of the PFAS are related
to Defence related activities that occurred within the boundaries of the property.
These included:
Ordnance Loading Areas, in particular OLA 3
and OLA8.
General Purpose Apron
Fire Station Building 7
Motor Transport Facility
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The timing, exact location and, mass of PFAS that historically discharged at source areas were not recorded
and therefore are not known. A summary of the information available from Defence personnel has been
documented above and in Appendix A.
The Aviation Fuel Farm and the Central Power Station were also identified as hosting extinguishers,
however, no training or servicing of that equipment was reported by Defence personnel to have occurred at
those locations. These facilities are down-gradient of the airfield, OLAs and Fire Station and therefore may
be migration pathways for potential contamination.
7.0 DATA QUALITY OBJECTIVES
As per Schedule B2 (Guideline on Site Characterisation) of the NEPM “a systematic planning process is
used for defining the objectives of a site assessment and to develop a sampling plan for the collection and
evaluation of representative data to achieve those objectives. Without systematic planning, the site
assessment may be ambiguous or inconclusive, which may lead to additional sampling requirements,
resulting in increased costs and project delays”.
In its simplest form, the planning process outlined in the NEPM should consider:
the overall objective of the site assessment,
the decision(s) to be made on the basis of the site assessment findings,
the constraints on the assessment (financial, time and logistical), and
the degree of flexibility to conduct follow-up investigations.
This project level information can then be used to identify the specific site information needed to address the
assessment objectives.
The Data Quality Objectives (DQOs) process is used to define the type, quantity and quality of data needed
to support decisions relating to the environmental condition of a site. The seven step DQO/data quality
indicator (DQI) process is identified in Schedule B2 of the NEPM as one example of a suitable systematic
planning approach for site investigations.
The DQO process involves the seven steps as follows:
Step 1: State the problem
Step 2: Identify the decision or goal of the investigation
Step 3: Identify the information inputs
Step 4: Define the site boundaries
Step 5: Develop the analytical approach
Step 6: Specify performance or acceptance limits
Step 7: Develop the plan for obtaining data.
The DQO process has been applied as described below, to ensure that data collection activities are
appropriate and achieve the stated objectives.
7.1 Step 1: State the problem
The original driver for the PSI was to address the identified data gaps associated with uncertainty on the
categorisation of RAAF Base Scherger.
Identified data gaps at RAAF Base Scherger prior to the PSI included:
Existence and use of bores in the vicinity of the property.
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Presence of PFAS in soil, groundwater, sediment and surface water on the site, at nominated potential
source areas and possible migration pathways.
Location and volume of AFFF foam training.
7.2 Step 2: Identification of the decision or goal of the investigation
The PSI was completed in accordance with the NEPM requirements for a Preliminary Site Investigation. The
assessment targeted specific data gaps for the property and the collection of environmental samples to
support the project objective.
The PSI was limited to use, storage and waste disposal associated with AFFF products and associated
potential PFAS contamination at the property.
7.3 Step 3: Identify the information inputs
For the PSI the major inputs were:
Existing reports and information relating to use, storage and waste disposal of AFFF, environmental
conditions (geology/hydrogeology etc.).
Existing investigations reports to confirm the environmental setting of the site including the presence of
available monitoring well locations, either located in the immediate vicinity of potential source areas or
at down-gradient of potential source areas.
Publically available historical information for the Property including:
Historic aerial photographs.
Topographical, soil and geological maps.
Site inspection and interview with Defence identified employees regarding the use, storage and
disposal of AFFF.
Collection of representative soil, sediment, surface water and groundwater samples, and laboratory
analysis of the samples at source locations.
7.4 Step 4: Define the investigation boundaries
The lateral boundaries of the investigation area are shown in Figure 1. The property has an area of
approximately 5,500 hectares.
The vertical boundaries of the investigation area were:
Soil - generally to a depth of 20 m.
Groundwater - the groundwater aquifer immediately underlying the site is at depth of approximately
10m, however it is expected to be seasonally variable.
Surface water – if present during the field investigation.
Sediments - in drainage lines to a depth of 0.15 m.
7.5 Step 5: Develop the analytical approach
The purpose of this step was to define the parameters of interest, specify action levels and combine the
outputs of the previous DQO steps to develop a series of options if certain trigger events occur.
A decision on the acceptance of the analytical data will be made on the basis of the DQI (Section 10.2).
The results of soil, sediment, surface water and groundwater analytical data were compared with the
adopted site criteria (Section 10.2) to assess the presence of PFAS at the property to support the re-
categorisation process.
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Contaminant concentrations in excess of the guidelines provided in Section 9.0 will be taken into
consideration in the re-categorisation process and may indicate the need for further investigation of human
health and environmental risk.
7.6 Step 6: Specify performance or acceptance limits
DQIs were developed based on the following PARCC parameters including:
P - Precision: A quantitative measure of the variability (or reproducibility) of data;
A - Accuracy: A quantitative measure of the closeness of reported data to the “true” value;
R - Representativeness: The confidence (expressed qualitatively) that data are representative of each
media present on site;
C - Completeness: A measure of the amount of useable data from a data collection activity, and
whether it is all the data required to enable the objectives to be met; and
C - Comparability: The confidence (expressed qualitatively) that data may be considered to be
equivalent for each sampling and analytical event.
The measures/criteria employed to enable review of these parameters are as follows and are detailed in
SAQP (Golder 2017).
Precision
Field precision was monitored through the use of Golder’s standard operating procedures and ensuring that
these were complied with throughout the sampling event(s). Suitable performance indicators for assessment
of laboratory precision include performance of intra-laboratory and inter-laboratory duplicate sample sets
through calculation of Relative Percentage Differences (RPD).
Accuracy (Bias)
Accuracy in the field activities was monitored through the use of SOPs and ensuring that these were
complied with throughout the sampling event(s). Furthermore, since PFAS are found in numerous items the
following special precautions will be taken during all sampling activities:
No use of TeflonTM containing materials (i.e. TeflonTM tubing, bailers, tape, plumbing paste);
No TyvekTM clothing were worn;
No clothing with stain or water resistant treatments (such as GoreTexTM) were worn;
No Post-ItTM Notes;
No fast food wrappers, aluminium foil, disposable cups or microwave popcorn were to be handled or
brought on site;
Hands were to be washed prior to any sampling activities after handling such items listed above, and
Nitrile gloves are to be worn during all sampling and sample handling activities; and
Chemical (blue) ice packs were not to be used.
PFAS can bind to glass, therefore all samples were collected into laboratory supplied high density
polyethylene (HDPE) or polypropylene containers.
The closeness of the reported data to the “true” value is assessed through review of performance of:
Method blanks, which are analysed for the analytes targeted in the primary samples;
Matrix spike sample sets;
Surrogate spikes; and
Laboratory control samples.
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Representativeness
To ensure the data produced by the laboratory is representative of conditions encountered in the field, the
following steps were taken:
Blank samples were run at the laboratory in parallel with field samples to confirm there are no unacceptable instances of laboratory artefacts;
Review of RPD values for field and laboratory duplicates to provide an indication that the samples were generally homogeneous, with no unacceptable instances of significant sample matrix heterogeneities; and
The appropriateness of collection methodologies, handling, storage and preservation techniques were assessed to ensure/confirm there was minimal opportunity for sample interference or degradation (i.e. volatile loss during transport due to incorrect preservation/transport methods/sampling technique for example).
Completeness
In assessing the completeness of the field data the following is considered:
All critical locations and depths sampled;
Representative samples collected; and
An appropriately experienced sampling team is engaged in the investigation program.
In validating the degree of completeness of the analytical data sets acquired during the program the
following was considered:
Whether SOPs for sampling protocols have been adhered to; and
Copies of all project chain of custody (COC) documentation are reviewed and presented.
Comparability
No prior investigations had assessed for the presence of PFAS in the sampling media analysed.
During the PSI, data was collected by experienced samplers and National Association of Testing Authorities,
Australia (NATA) accredited laboratory methodologies were employed in all laboratories.
7.7 Step 7: Develop the plan for obtaining data
Sample locations were selected based on the observed site conditions and on the site history established
from interviews with Defence personnel. The investigations may identify further areas requiring assessment
and thus the overall approach would be modified as required following refinement of the preliminary CSM
presented in SAQP (Golder 2017). The broader sampling strategy is presented in Table 9 and proposed
locations are shown in Figure 3-1 to Figure 3-16. A key map showing the extent of figures prepared across
the property is provided as Figure 3A. Changes to the sampling and analytical plan are discussed in
Section 8.0.
Table 9: Proposed Source Area Sampling Strategy
Source Media Sampling Strategy
Ordnance
Loading Areas
(OLA)
(Figure 3-3)
Soil One borehole each for OLA3 (BH024 / MW024) and OLA8 (BH025 / MW025).
2 soil samples per bore (shallow and deep).
Groundwater Two groundwater samples were collected from new monitoring wells installed at each OLA and sampled (MW024 and MW025).
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Source Media Sampling Strategy
Surface water/sediment Collection of 1 surface water and 1 sediment sample at location along drainage pathways that flow south from OLA3 (SW001/SD001) and OLA8 (SW002/SD002).
However no surface water was present at the time of sampling so only sediment samples were collected.
General Purpose Apron (GPA)
(Figure 3-5)
Soil One borehole (BH022) drilled and collection of 2 soil samples (shallow and deep).
Groundwater Borehole converted into groundwater well (MW022) and sampled
Surface water/sediment Collection of 1 surface water and 1 sediment sample at location along drain that flows south-east from the GPA (SW010/SD010) and at location in interceptor basin on western side of GPA SW003/SD003).
However no surface water was present at the time of sampling so only sediment samples were collected.
Fire Station Building 7
(Figure 3-6)
Soil 1 borehole in the apron of the helipad opposite Building 7 (on eastern side of road, south of access road to helipads) (BH023) and collection of 2 soil samples (shallow and deep).
Groundwater Borehole converted into groundwater well (MW023) and sampled.
Surface water/sediment Collection of 1 surface water and 1 sediment sample at location immediately south of Building 7 (SW004/SD004).
However no surface water was present at the time of sampling so only sediment sample was collected.
Aviation Fuel Farm
(Figure 3-4)
Groundwater Sampling of 1 existing monitoring well (RAAFSGR10) outside of the perimeter fence of the Aviation Fuel Farm compound.
Note the Aviation Fuel Farm is inferred downgradient of the OLAs.
Motor Transport Facility
(Figure 3-9)
Groundwater Sampling of 2 existing monitoring wells, (RAAFSGR18 and RAAFSGR19) at the northern end of the compound.
Although not considered primary sources, sampling was proposed at areas close to neighbouring land
borders and along potential contamination pathways and/or potential receptors as outlined in Table 10.
Table 10: Receptor and Pathway Sampling
Pathway/Receptor Media Sampling Strategy and Access/Limitations
Central Power Station (Figure 3-7)
Groundwater Sampling of 1 existing monitoring well (RAAFSGR14) on the western side of road.
Retention Basin
(Figure 3-8)
Surface water/
sediment
Collection of 1 surface water and 1 sediment sample at retention basin (SW005/SD005).
However no surface water was present at the time of sampling so only sediment sample was collected.
Water treatment plant (Figure 3-10)
Water Collection of 1 sample of bore water at entry to treatment plant (W001) (combined flow from water
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Pathway/Receptor Media Sampling Strategy and Access/Limitations
supply bores 3 and 4) and 1 sample from treated water (W002).
Sewage Treatment Plant
(STP)
(Figure 3-13)
Groundwater
Sampling of 1 existing monitoring well (historical bore “BH34”) down-gradient of STP, near western boundary. BH34 could not be located during the field program and was not sampled.
South-western portion of Base
(Figure 3-11)
Soil One borehole drilled on access road to the Sewage Treatment Plant. (BH026) and collection of 2 soil samples (shallow and deep).
Groundwater Borehole converted into groundwater well (MW026) and sampled.
North-western portion of Base
(Figure 3-2)
Soil 1 borehole near site boundary (BH027) and collection of 2 soil samples (shallow and deep).
Groundwater Borehole converted into groundwater well (MW027) and sampled.
Creek – south-western portion of Base
Near site boundary with Peppin community (Figure 3-13)
Surface water/
sediment Collection of 1 surface water and 1 sediment sample at location near fenceline boundary with neighbouring Peppin community who use surface/groundwater intermittently for domestic purposes (SW006/SD006).
The proposed location was inaccessible therefore samples were collected slightly down-stream on this creek (north-west).
Creek – central portion of Base
(Figure 3-7)
Surface water/
sediment
Collection of 1 surface water and 1 sediment sample (SW007/SD007) from Creek (fed from Spring no. 2) downgradient of potential airfield source areas near discharge from retention basin.
The creek was inaccessible due to the presence of a large fence and dense scrub. The revised sample location was from the drainage pathway in the vicinity of Building 7 and Central Power Station which is different drainage flow path to the proposed samples.
Creek – western boundary
(Figure 3-12)
Surface water/
sediment
Collection of 1 surface water and 1 sediment sample (SW008/SD008) in Creek adjacent to Sewage Treatment Plant (STP), close to western boundary.
The location was inaccessible due to the presence of Croton Hirtus. Therefore the sampling location was moved closer to STP (and not on creek line). No surface water was present so only sediment sample was collected
Creek in north-western portion of Base
(Figure 3-1) Surface water/
sediment
Collection of 1 surface water and 1 sediment sample (SW009/SD009) at the confluence of two creeks close to northern boundary.
The target location was inaccessible therefore a revised location representing the northern tributary of proposed location was chosen.
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8.0 SAMPLING, ANALYSIS AND QUALITY PLAN
A Sampling, Analysis and Quality Plan (SAQP) was prepared for this investigation as documented in the
report titled RAAF Base Scherger (1218) Sampling, Analysis and Quality Plan, dated 13 April 2017.
The SAQP includes comprehensive description of the sampling methods and field procedures adopted for
the site investigation.
The SAQP was implemented as proposed with the following deviations noted:
Locations SW001 to SW005 inclusive, as well as SW008 and SW010 did not have surface water at the
time of sampling. Therefore no water sample was obtained. However, sediment samples were however
still collected from these locations.
Additional surface water and sediment sampling locations (SD/SW011 to SD/SW013) were added to
the program following the issue of the SAQP in response to several proposed locations being relocated,
inaccessible or dry. The rationale for including these new locations is described below:
Collection of 1 surface water and 1 sediment sample (SW011 and SD011) at the western portion of
Base within drainage flow pathway downstream of the operational areas on base ( (Figure 3-15)
Collection of 1 surface water and 1 sediment sample (SW012 and SD012) at the creek near
western boundary downstream of the operational areas on base (Figure 3-14)
Collection of 1 surface water and 1 sediment sample (SW013 and SD013) from an un-named creek
north of the runway near the source of Spring no. 4. (Figure 3-16).
Locations SD/SW006, SD/SW007, SD/SW008 and SD/SW009 were moved from their original planned
locations due to access limitations onsite, as described in Table 11.
A groundwater sample was intended for collection from Sewage Treatment Plant (RAAFSGR34 or
BH34) however the bore could not be located due to the presence of dense scrub and suspected
Croton Hirtus weed.
These deviations from the SAQP are not considered to affect the outcome of the assessment and the
objectives of the PSI can still be met.
9.0 ASSESSMENT CRITERIA
Given the preliminary nature of the investigation and the preliminary identification of receptors, the analytical
results are screened against an adopted set of guideline values as part of a Tier 1 screening level
assessment which includes both health based and ecological based criteria
The Defence project guidelines (Defence Contamination Directive #8 (DCD8), Amendment 1 and 2, DoD
Sept 2016 and May 2017) for poly and per-fluoroalkyl substances have been adopted for this PSI.
Complementing DCD8, supplementary criteria have been selected to support the assessment for ecological
protection exposure pathways not referenced in DCD8 from the following Guideline:
Draft Commonwealth Environmental Management Guidance on PFOA and PFOS (Department of the
Environment and Energy, 2016) for the protection of ecological values.
Consistent with the RAAF Scherger EMP framework and the water quality field measurements, the 99% level
of species protection for freshwater ecosystems has been selected as the adopted criteria. Due to limits of
laboratory detection methods, the laboratory detection limit will be used as a practical standard.
Aside from the stage of the investigation being preliminary, it was considered appropriate to nominate both
human health (given the water supply) and ecological (aquatic waterway spring) receptors have been
identified onsite.
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Table 11: Adopted Soil, Sediment, Groundwater and Surface Water Screening Values
Exposure Scenario PFOS/PFHxS PFOA 6:2FTS
Soil and Sediment
Health-based screening levels (direct contact only) – Residential
6 mg/kg*/** 16 mg/kg* 60 mg/kg*
Groundwater and Surface water
Health Based Guidance - Drinking water quality value
0.07 µg/L*** 0.56 µg/L*** 5.0 µg/L*
Health Based Guidance -Recreation Water Quality
0.7 µg/L*** 5.6 µg/L*** 50 µg/L*
Protection of Environmental Values – Freshwater 99 % species protection
0.00023 µg/L** 19 µg/L -
Notes: * DCD8 – Amendment 1 ** - PFOS only ***DCD8 –Amendment 2 µg/L – microgram per litre mg/kg- milligram per kilogram PFHxS - Perflurohexane sulfonic acid 6:2 FTS – 6:2 Fluorotelomer sulfonic acid
The soil guideline values were adopted for sediment samples as a guide only for the PSI.
10.0 RESULTS FIELD PROGRAM
The field investigation program was conducted between 2 May 2017 and 17 May 2017. The findings of the
field and analytical programs are presented in the following sections. The sample locations are presented in
Figures 3A (key map) and Figures 3-1 to 3-16. Details of the soil stratigraphy and soil sampling intervals
are included in soil bore logs in Appendix F. Data validation summary sheet is presented in Appendix G
and the laboratory certificates, chain of custody sheets and sample receipts are presented in Appendix H.
Concentrations of PFOS in groundwater are illustrated on Figures2 4-2 to 4-5, 4-7 and 4-9.
Concentrations of PFOS in sediment and surface water are illustrated on Figures3 5-3, 5-5 to 5-8 and 5-16.
Figure 6 provides an overview of the surface water and groundwater results for both PFOS and PFHxS.
10.1 Description of Site Conditions
10.1.1 Soils
Subsurface conditions were investigated at six locations across the Base:
General Purpose Apron (BH022)
Fire Station Building 7 (BH023)
Ordnance Loading Area 3 (BH024)
Ordnance Loading Area 8 (BH025)
South-western portion of site on access road to Sewage Treatment Plant (BH026)
North-western portion of site near site boundary (BH027)
22Figure 4 (Concentrations of PFOS in groundwater) comprises 6 sub-maps, following the subset map numbering of Figure 3.
33Figure 5 (Concentrations of PFOS in surface water and sediment) comprises 6 sub-maps, following the subset map numbering of Figure 3.
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The boreholes were drilled using air hammer to a total depth ranging 13.5 m (BH027) and 22.5 m (BH022,
BH024, BH025).
Geological logs for each borehole are provided in Appendix F. Following drilling, each well was converted to
a groundwater monitoring well (MW022, MW023, MW024, MW025, MW026 and MW027).
Fill material was encountered at BH022 (GPA) and BH024 (OLA3) to a depth of 0.4 m and 0.9 m only, and
comprised primarily of clayey gravelly sand.
Lithology encountered at BH027 was primarily silty clays. BH027 is located on the north western extent of
the Base, at a lower elevation than other areas investigated. Soils encountered at all other bores varied
intermittently between clayey sand, clayey gravelly sand and silty sand, varying to sandy clays in some parts
of the Base. White sand and kaolin clay clasts are present at depth. The shallow horizon, described as
sandy clayey gravel, silty clay or silty sand was found up to approximately 1.2 m depth.
10.1.2 Groundwater
Groundwater was assessed in the following areas:
Aviation Fuel Farm (RAAFSGR10)
Central Power Station (RAAFSGR14)
Motor Transport Facility (RAAFSGR18, RAAFSGR19)
General Purpose Apron (MW022)
Building 7 (MW023)
Ordnance Loading Area 3 (MW024)
Ordnance Loading Area 8 (MW025)
South-Western locality of Base (MW026)
North-western portion of site near site boundary (MW027)
Bore water was sampled from the Water Treatment Plant (WTP) pre-treatment (W001) and post-
treatment (W002).
Gauging data and field water quality results are provided in Tables A and B (attached).
New monitoring wells and monitoring wells sampled in this investigation were surveyed to establish their
height datum and location. The report provided by the surveyor is included as Appendix I.
Depth to groundwater ranged 5.1 metres below top of casing (mtoc) (RAAFSGR19) to 14.02 mbtoc (MW24).
Groundwater elevations ranged 39.1 m AHD (RAAFSGR18) to 15.7 m AHD (MW027). Based on the current
monitoring data, groundwater is inferred to flow in a west to northwest direction, towards Mission River.
GHD (1998) identified that groundwater flow direction within the upper aquifer was considered to be towards
the west, with a calculated groundwater flow rate (permeability or k value) for the shallow aquifer estimated
at approximately 30 m/day, confirmed by Maunsell in 2005.
Groundwater was typically fresh and slightly acidic, with conductivity (EC) values ranging from 17.50 S/cm
(RAAFSGR18) to 87.8 S/cm (RAAFSGR14) and pH values ranging 4.52 (MW024 – 5.64 (MW026). There
were no noticeable odours or sheens, and non-aqueous phase liquid were not encountered in the
observation wells sampled.
Water samples collected from the water treatment supply, pre- and post- treatment were fresh (22 S/cm -
27 S/cm) and slightly acidic (5.21 – 6.53 pH).
10.1.3 Surface water and Sediment
Sampling and analysis of six surface water and 13 sediments was undertaken from natural and formed
surface drainage features around the Base. The intention in the SAQP was for sediment and surface water
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samples to be co-located. Where surface water was present, this occurred. In some locations, only sediment
samples could be collected. Sampled areas included:
Ordnance Loading Area 3 (SD001 sediment only, drainage channel dry) (Figure 3-3)
Ordnance Loading Area 8 (SD002 sediment only, drainage channel dry) (Figure 3-3)
General Purpose Apron (SD003 and SD010 sediment only, drainage channel dry) (Figure 3-5)
Fire Station Building 7 (SD004 sediment only, drainage channel dry) (Figure 3-6)
Retention Basin (SD005 sediment only, drainage channel dry) (Figure 3-4)
Creek – south west portion of Property, slightly down-stream from location of where Peppin community
occasionally camp (SW006 and SD006) (Figure 3-13)
Creek near road crossing which is part of drainage pathway from Building 7 locality and CPS locality
(SW007 and SD007) (Figure 3-7)
Western property boundary near Sewage Treatment Plant (SD008 sediment only, drainage channel
dry) (Figure 3-12)
Creek in north west portion of property near northern site boundary (SW009 and SD009) (Figure 3-1)
Western portion of property within drainage flow pathway downstream of the operational areas on base
(SW011 and SD011) (Figure 3-15)
Creek near western boundary downstream of the operational areas on base (SW012 and SD012)
(Figure 3-14)
Unnamed creek north of the runway near the source of Spring no. 4 (SW013 and SD013). (Figure 3-16)
Measurements of electrical conductivity from surface water samples indicated that the water is fresh, ranging
from 3 mg/L to 26 mg/L. pH was also reported at slightly acidic conditions from the surface water samples.
Sediments from the site water features consisted predominantly of silty sands with some organic matter.
Creek and drainage channels throughout the site are highly vegetated. The sediments in creek and drainage
channels were predominantly a combination of decaying organic matter and silty sands (generally brown in
colour).
Surface water quality parameters are provided in Table B (attached).
10.2 Data Validation
10.2.1 Data Quality Indicators for Field Program
The details of the data validation assessment are included in Appendix G.
Data quality indicators (DQIs) for the field work sampling and analysis were implemented to ensure data is
valid and complete for the site assessment and that the DQO (Section 7.0) have been met. DQIs included
the following:
The sampling program has obtained samples from the nominated media at the investigation locations
where possible to do so. Section 8.0 confirms the proposed samples that could not be collected;
The Laboratory Limit of Reporting (LOR) were below the adopted criteria where technically possible.
The adopted criteria for protection of ecological receptors for waters was lower than the available
laboratory LOR.
Sample preservation, storage, and holding time of samples were within acceptable limits;
Field and analytical laboratory sample Chain-of-Custody (CoC) procedures and documentation were
completed;
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Analytical results for replicated samples, including field and laboratory duplicates and inter-laboratory
duplicates, expressed as Relative Percent Difference (RPD) were within the nominated acceptance
criteria for field duplicates and splits. Australian Standard AS4482.1-2005 (SA 2005) indicates that
acceptable results are indicated by a RPD of better than 30 to 50 %, but notes that the variation can be
expected to be higher for organic analytes than inorganic analytes, and higher where there are low
concentrations of analytes. Tiered acceptance criteria have been adopted for assessment of RPDs as
follows:
Results < 10 times LOR: any RPD are acceptable;
Results ≥ 10 times and < 20 times LOR : RPD < 50% and
Results ≥ 20 times LOR: RPD < 30%.
Rinsate blanks were collected at the frequencies outlined in SAQP to assess the potential for cross-
contamination during field sampling. PFOS was detected in rinsate water samples QC305 and QC309
(0.003 g/L respectively). This concentration is only marginally above the LOR of 0.002 g/L. QC305
was collected from auger wash water after drilling BH023 on 10/05/2017. QC309 was collected from
dip meter wash water after sampling new groundwater wells on 15/05/2017. The positive identification
in these samples may represent an overestimation or false positive of PFOS in primary samples. Given
the number of samples reported below the laboratory limits of reporting, this is not considered to be a
significant issue to question data quality; and
Laboratory spikes, controls and surrogates targeted were within 70% and 130%, demonstrating the
reliability of the laboratory results reported.
Precision and Accuracy (Bias)
Following completion of the field program, the information collected was checked, collated, and summarised
in tabular form. The results of the laboratory analyses have been assessed and validated progressively using
recognised QA procedures.
The primary objective of the data validation process has been to ensure that the data reported can be used
to achieve the project objectives.
The validity of the analytical data reported has been assessed by a critical review of the QC check sample
results. The validation process is based upon the following data validation guidance documents:
National Environment Protection (Assessment of Site Contamination) Measure 1999 (NEPC 2013);
USEPA Contract Laboratory Program National Functional Guidelines for Superfund Inorganic Data
Review (US EPA, 2010); and
USEPA Contract Laboratory Program National Functional Guidelines for Superfund Organic Methods
Data Review (US EPA, 2008).
Accuracy and precision measurements from the appropriate QC check samples have been compared with
the analytical DQOs to assess the quality of the analytical data. Data validation records are presented in
Appendix G.
Representativeness
The data produced by the laboratories was representative:
Method Blanks – Analytes were not detected above the Laboratory Limit of Reporting (LOR);
Field Duplicate RPDs (interlaboratory and intralaboratory) - Review of RPD values for field and
laboratory duplicates provided an indication that the samples are within the acceptable limits.
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Fieldwork - decontamination procedures were undertaken at each location. Three rinses (1x tap water,
2x DI water) were used to clean instruments and tools. For soil work, scrubbing with wire brush (metal)
then rinsing was completed; and
Samples - were handled, stored and transported in accordance with the requirements NEPC (1999).
Samples were transported under full chain of custody documentation. The laboratory returned a copy of
the signed COC acknowledging the receipt data and time and identity of samples included in the
shipment.
Completeness and Comparability
In order to assess comparability, field sampling procedures, laboratory sample preparation procedures,
analytical procedures and reporting limits were similar to established protocols.
10.2.2 Data Validation Conclusion
The QA/QC program and quality of the analytical data is considered to be sufficient for environmental
interpretation and to allow the objectives of the investigation to be assessed.
10.3 Laboratory Analysis
Soil, groundwater, surface water and sediment samples were submitted to the nominated laboratories for
analysis. Laboratory results are summarised and presented against adopted screening criteria in Table C
(groundwater), D (surface water), E (water supply) and F (sediments and soil). Laboratory reports (ALS
batch number EB1709386, EB1709387, EB1710297 and EB1709388, and Eurofins batch number 546883)
and chain of custody documentation is provided in Appendix H.
A summary of the soil, sediment, surface water, groundwater and tap water samples (including QC sampling)
submitted for PFAS laboratory analysis is presented in Table 12 below.
Table 12: Number of Environmental Samples Analysed for PFAS
Parameter Primary QA/QC
Soil 12 5
Sediments 13 2
Surface Water 6 1
Groundwater 10 2
Tap Water 2 1
Note: QA/QC samples comprise duplicate and triplicate samples. In addition rinsate samples were analysed.
Laboratory analysis was conducted in accordance with the standard NATA certified test methods outlined in
Schedule B(3) of the NEPM (NEPC 2013) or equivalent modified methods supported by adequate quality
control.
The laboratories for this investigation were:
ALS Environmental Laboratory for primary soil, sediment and water samples and intra laboratory
duplicate samples; and
Eurofins MGT for inter-laboratory duplicate samples.
10.3.1 Soil Results
Soil samples were collected between 0.5 and 1.0 m below ground level (m bgl), and a deeper sample
targeting just above the water bearing zone to a total depth of between 7.25 m and 16.75 m bgl.
The soil sample analysis results are presented in Table F and summarised in Table 13 below for specific
PFAS compounds where assessment criteria have been adopted.
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Table 13: Summary of laboratory soil results – PFAS
No of Samples Analysed
Analyte Maximum Concentration (mg/kg)
No. of Samples with Detections above Laboratory LOR
Exceeded adopted Criteria
17 Perfluorooctanoic Acid
(PFOA)
0.0002 (ALS)
<0.005 (Eurofins) 1 Nil
17 Perfluorooctane sulfonic
acid (PFOS)
0.0231 (ALS)
<0.005 (Eurofins) 2 Nil
17 Perfluorohexane sulfonic
acid (PFHxS)
0.0005 (ALS)
<0.005 (Eurofins) 1
No criteria adopted
17 6:2 Fluorotelomer sulfonic
acid (6:2 FTS)
<0.0005 (ALS)
<0.01 (Eurofins) 0 Nil
Concentrations of PFAS in soil samples were below the adopted screening criteria in the investigated areas
at the property.
10.3.2 Groundwater Results
The groundwater sample analysis results are presented in Table C and summarised in Table 14 below.
Table 14: Summary of laboratory groundwater results – PFAS
No of Samples (Primary) Analysed
Analyte Concentra-tion Range (µg/L)
No. of Primary Samples with Detections above Laboratory LOR
Exceeded Human Health - Drinking Water Quality
Exceeded Ecological Values – Freshwater (99 % Species Protection*) (µg/L)
12 PFOA <0.002 to
0.023 Nil Nil
12 PFOS <0.002 to
0.073 7 No criteria adopted
0.036 (RAAFSGR10)
0.026 (RAAFSGR14) 0.034 (RAAFSGR18) 0.008 (MW022) 0.023 (MW024) 0.073 (MW025) 0.003 (MW027)
12 PFHxS <0.002 –
0.106 6 No criteria adopted No criteria adopted
12 Sum of PFHxS
and PFOS (calculated)
<0.002 - 0.179
8
0.086 µg/L (RAAFSGR10)
0.179 µg/L
(MW025)
No criteria adopted
12 6:2 6:2 FTSA <0.005 –
0.046 2 Nil No criteria adopted
Note: Duplicate or Triplicate results assessed as a conservative measure where the concentration was
higher.
A summary of the exceedances by each geographical part of the property were as follows:
Aviation Fuel Farm (RAAFSGR10) -Concentrations of PFAS compounds were detected with the sum
of PFHxS and PFOS exceeding the adopted drinking water criteria. Reported concentrations for PFOS
were above the Protection of Environmental Values – Freshwater 99 % species protection criteria.
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Central Power Station (RAAFSGR14) - Concentrations of PFAS compounds were detected with the
reported concentrations for PFOS exceeding the Protection of Environmental Values – Freshwater
99 % species protection criteria.
Motor Transport Facility (RAAFSGR18, RAAFSGR19) - Concentrations of PFAS compounds were
detected with the reported concentrations for PFOS exceeding the Protection of Environmental Values
– Freshwater 99 % species protection criteria.
General Purpose Apron (MW022) - Concentrations of PFAS compounds were detected with the
reported concentrations for PFOS were above the Protection of Environmental Values – Freshwater
99 % species protection criteria.
Building 7 (MW023) - Concentrations of PFAS compounds were not detected in groundwater collected
in the vicinity of Building 7.
Ordnance Loading Areas (MW024, MW025) - Concentrations of PFAS compounds were detected at
each sample location in the Ordnance Loading Areas. Reported concentrations for sum of PFHxS and
PFOS were above the adopted drinking water criteria at MW025. Reported concentrations for PFOS
were above the Protection of Environmental Values – Freshwater 99 % species protection criteria at
both MW024 and MW025.
South Western Portion of Base (MW026) - Concentrations of PFAS compounds were not detected in
groundwater at MW026.
North-Western Portion of site near site boundary (MW027) - Concentrations of PFAS compounds
were detected with the reported concentrations for PFOS exceeding the Protection of Environmental
Values – Freshwater 99 % species protection criteria.
Water Treatment Plant (W001, W002) - Concentrations of PFAS compounds were not detected in
either the treated or untreated sample from the water treatment plant.
10.3.3 Sediment and Surface Water Results
Surface Water
The surface sample analysis results are presented in Table D and summarised in Table 15 below.
Table 15: Summary of laboratory surface water results – PFAS
No of Samples Analysed
Analyte Concentration Range (µg/L)
No. of Samples with Detections above Laboratory LOR
Exceeded Human Health - Recreational water quality value
Exceeded Ecological Values – Freshwater (99 % Species Protection*)
6 PFOA <0.002 (all LOR)
0 Nil Nil
6 PFOS <0.002 -0.003 1 No criteria adopted
0.003 µg/L
(SW013); however LOR is higher than
adopted criteria
6 Sum of PFHxS and PFOS (calculated)
<0.002 – 0.003 1 Nil No criteria adopted
6 6:2 FTSA <0.005 0 Nil No criteria adopted
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The only PFAS compound detected in all the surface water samples was PFOS, collected from the unnamed
creek north of the runway (SW013).– The reported concentration of PFOS exceeded the adopted guidelines
for the protection of freshwater aquatic ecosystem (Environmental Values) at this location.
Sediment
The sediment sample analysis results are presented in Table F and summarised in Table 16 below.
Table 16: Summary of laboratory sediment results – PFAS
No of Samples (Primary) Analysed
Analyte Concentration Range (mg/kg)
No. of Primary Samples with Detections above Laboratory LOR
Exceeded the Criteria
13 PFOA <0.0002 - 0.0004 1 Nil
13 PFOS <0.0002 - 0.003 9 Nil
13 6:2 FTSA <0.0005 0 Nil
10.3.4 Investigation Derived Waste
Surplus soil from the drilling and installation of groundwater monitoring wells was transferred to an on-site
quarry pit designated for temporary stockpile of soils. The dedicated stockpile was placed on a plastic liner
and covered. Samples of the investigation derived waste were analysed for characterisation (refer photo in
Appendix B). A volume of investigation derived soil waste in order of 6 m3 was generated and three primary
samples collected. Low concentrations of PFOS were detected in the samples at concentrations close to the
LOR (reported concentration of 0.002 mg/kg to 0.0024 mg/kg).
11.0 CONCEPTUAL SITE MODEL
The revised PFAS conceptual site model (CSM) is based on the initial CSM presented in the SAQP (Golder
2017) and was revised with the results of the PSI. The sampling and analysis undertaken as part of the PSI,
is based on the CSM which was prepared using the information predominantly gained through Site
inspections and interviews undertaken as part of this PSI. The sample locations targeted the areas
considered most likely to host PFAS contamination, however, it not a comprehensive investigation.
The initial CSM aims to provide an understanding of the potential for exposure to the PFAS contamination.
A potential risk can only exist where confirmed sources and receptors are linked by a complete exposure
pathway. Based on the objectives of the PSI the CSM only considers PFAS.
A visual schematic of the conceptual site model is provided as Figure 7.
11.1 Sources
PFAS detections were reported in the following media:
Shallow soil (upper 1m) at the General Purpose Apron, Building 7 and OLA8;
In sediment samples collected in the operational parts of the property including the OLA3, OLA8, GPA,
Fire Station Building 7, Retention Basin and downgradient of the Central Power Station. Sediment
samples collected closer to the western and northern property boundaries did not report PFAS
detections.
In surface water at SW013 located north of the runway and near Spring no. 4. (All other surface water
samples collected along the downgradient western boundary creeks were reported below LOR.)
In all groundwater samples, excluding the monitoring well installed at Building 7 and at the monitoring
well in the south-west portion of the property. Concentrations of PFHxS/PFOS were relatively higher at
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OLA8, Aviation Fuel Farm, the Central Power Station and the Motor Transport Facility compared to
other locations monitored on-property.
PFAS was not detected in the 2 water supply samples collected at the water treatment plant.
A number of PFAS source areas were identified. As a general remark, Defence personnel indicated that the
extent of AFFF usage was reasonably limited at this bare Base in that the conduct of foam training was
limited to one event during the Exercise Kakadu in 2005. Other AFFF usage has been associated with the
servicing of fire extinguishers and associated waste disposal.
Identified PFAS sources were as follows:
OLAs, in particular OLA 3 and OLA8
The review of historical documents and interviews with current and former base personnel indicated that there has been routine servicing of fire extinguishers where waste AFFF was historically discharged to ground.
During the PSI, two groundwater samples were collected in the vicinity of the OLAs. PFAS detections in
groundwater found in this locality are at concentrations exceeding the criteria for protection of ecosystems
(and also exceeding the drinking water criteria at OLA8). Shallow soils and sediment results also indicated
detections of PFAS.
General Purpose Apron
Routine servicing of fire extinguishers where waste AFFF was historically discharged to ground was also identified to occur at the GPA. Concentrations of PFAS compounds were detected in shallow soil, sediment and groundwater in this area indicating that PFAS have migrated through the soil profile to groundwater.
Aviation Fuel Farm
Analysis of groundwater collected from an existing well in the area confirmed the presence of PFAS in groundwater in this area at elevated concentration of PFHxS/PFOS sum exceeding the drinking water criteria.
Fire Station Building 7 and surrounds
Interview information from Defence personnel indicated that a foam capability fire truck was stationed here during the short duration whilst Exercise Kakadu was conducted in 2005. Concentrations of PFAS compounds were detected in shallow soil and sediment samples, however it was not detected in groundwater collected in the vicinity of Building 7.
Motor Transport Facility (northern end of compound and Building 707).
The Motor Transport Facility is considered a potential source due to a once off observation of waste AFFF being discharged at northern end of compound. Additionally, foam capability truck had been routinely stored in Building 707. Groundwater analysis of existing wells in the area confirm that concentrations of PFAS compounds were detected at both sample locations in the Motor Transport Facility.
11.2 Migration Pathways
PFAS may migrate through the environment in migration pathways as dissolved species with water
undergoing processes such as desorption, adsorption, leaching, or bioaccumulation.
Surface impacts may be associated with deposition/adsorption of PFAS to soil from use of AFFF or from
overland flow of waste water. PFAS may migrate in stormwater and surface water that flows along drainage
lines into nearby dams, wetlands, or other surface water bodies.
The results of the program identified the presence of PFAS in the sediment of drainage channels in the
vicinity of the OLAs, GPA and Motor Transport Facility. PFAS was identified in surface water collected north
of the runway, which may indicate an additional source area in the vicinity, or that PFAS is migrating along
these flow paths.
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The presence of PFAS in the groundwater indicates that PFAS has migrated to the groundwater, likely to be via rainwater infiltration leaching PFAS present in the surface soils or pore water.
11.3 Exposure Pathways
The following exposure pathways are considered to be relevant:
Dermal contact or ingestion of impacted soil and sediment. Generally, direct contact with soils is limited
to the top 0.5 m, although construction or intrusive workers may disturb and be exposed to deeper soils.
Dermal contact or ingestion of impacted surface water or groundwater. Groundwater may be accessible
when extracted for uses such as domestic, irrigation or other purposes. Recreational use of surface
water in tributaries may occur off-property.
Ecological receptors present within the surface waters of tributaries and creeks. Aquatic receptors
present in Mission River may be exposed to impacted surface water.
Ingestion of food items grown with or within impacted surface water or groundwater. Such as,
recreational fishing within Mission River.
11.4 Receptors There are registered bores in the area for the extraction of water, which may be used for drinking water supply or agricultural use. The use of surface water or groundwater for drinking water is considered to be high since the local region is not connected to reticulated water supply.
Potential human health and ecological receptors for both on-property and off-property locations are
presented in Table 17 below. The receptors listed are those considered to be present either on- or off-
property, however, may not be at risk from exposure to PFAS contamination as an exposure pathway may
be incomplete.
Table 17: Potential Human Health and Ecological Receptors
Human Health Ecological
On-Property
Defence Personnel / Contractors, including users of bore water
Visitors
Intrusive, construction or maintenance workers
Aquatic Ecological Receptors
Terrestrial Ecological Receptors
Off-Property
Residents of the Peppin Community
Intrusive, construction or maintenance workers
Users of bore water
Consumers of impacted biota (e.g fishing)
Recreational Uses of Surface water (e.g swimming). Although swimming cannot be excluded, the region is not well known for use of surface water for swimming given the crocodile risk.
Terrestrial Ecological Receptors
Aquatic Ecological Receptors
Based on an initial screening of potential linkages between source, pathway and receptors and considering
the exposure pathways outlined in Section 11.3, the sub-set of potential receptors presented in Table 18 are
considered to represent potentially complete linkages between contamination sources and receptors.
Table 18 has not included possible off-property receptors given the absence of investigation results to
confirm if there are complete linkages between on-site sources and off-property receptors.
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It is noted that there is a confirmed history of off-property use of groundwater and surface water for drinking
water supply at the Peppin community. Whilst access to preferred sampling locations onsite near to the
Peppin area was not possible due to a lack of access tracks, the nearest sampling locations in both
groundwater (MW026) and surface water (SW006) reported non-detect concentrations of PFAS. It is noted
that the Peppin Community is located some 3 km from the potential source areas on the property and is not
down-gradient of these potential source areas based on the available data of the inferred groundwater and
surface water flow directions.
Additionally, the adjacent mine may extract water for drinking water supply. Surface water sampling locations
closest to the western boundary adjoining the mine reported non-detectable concentrations of PFAS.
These potential receptor groups have not been included in Table 18 given the absence of off-property PFAS
data. However, it is considered that any future investigation / risk assessment would further consider all
potential receptors to further develop the understanding of the CSM in the event additional data will be
available for evaluation.
Table 18: Possible Receptors based on Potentially Complete Source, Pathway Receptor Linkages
Human Health Ecological
On-Property
Intrusive, construction or maintenance workers (potential contact with contaminated soil/sediment/surface water/sediment). There is no adopted criteria available for this particular exposure scenario (ie intrusive, construction or maintenance workers), however it is noted that the soil and sediment concentrations detected were less than the adopted criteria for residential land use.
Domestic use of bore water.
It is noted that the limited sampling (one sample of each raw and treated water) at the water supply plant reported no detections of PFAS. Furthermore, the closest detection of PFAS to the water treatment plant is approximately 600m at the Motor Transport facility. Based on the inferred groundwater flow directions (westerly), the Motor Transport facility is likely to be cross gradient from the onsite water supply plant. However, the operation of the groundwater extraction system will induce a groundwater gradient towards the well during operation, however, the extent of the zone of influence and the depth (well screen) of this extraction, is not known.
Aquatic Ecological Receptors (fish etc living in wetlands and tributaries).
Terrestrial Ecological Receptors
In terms of surface water concentrations, samples collected were reported non-detect concentrations other than in the stream on the northern side of the runway (SW13).
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11.5 Data Gaps
The following key data gaps have been identified to consider in further assessment:
Delineation of the extent of PFAS in soil, sediment, surface water and groundwater in the vicinity and
down-gradient of the source areas.
Confirm specific use of groundwater from off-site wells and off- site surface water.
Review of existing information of the set-up and operation groundwater extraction system. Information
to evaluate could include well construction for pumping wells (particularly well screen interval), pumping
routines in different base occupancy situations, geological/hydrogeological information/data.
Use of Mission River for recreational purpose and/or for recreational fishing.
12.0 CONCLUSIONS AND RECOMMENDATIONS
12.1 Conclusions
The PSI was completed in accordance with the National Environment Protection (Assessment of Site
Contamination) Measure (ASC NEPM) (NEPC, 2013) including the collection of target environmental
samples.
The PSI historical review has refined the understanding of the history of AFFF use, storage and waste
disposal and identified potential primary sources of PFAS contamination. Given the nature of the property
being a “bare” Base with a small rotating workforce, firm details of the historical usage of AFFF could not be
established with a high degree of certainty based on the interviews conducted and as such, there may be
other primary source areas where AFFF was used, stored or disposed. Nonetheless, given the “bare” Base
nature of the property, there has been limited usage of AFFF in that conduct of foam training was limited to
one event during the Exercise Kakadu in 2005. Other AFFF usage has been associated with the servicing of
fire extinguishers and associated waste disposal.
The intrusive investigation including the collection of soil, sediment, surface water and groundwater at
targeted locations provided data to confirm that the operations undertaken have led to the presence of PFAS
contamination. The reported laboratory data suggests that PFAS contamination has migrated from the
identified sources areas, however the extent of this cannot be assessed based on the scope of the PSI. The
current understanding of source areas, potential migration pathways and receptors is presented in the CSM
in Section 11.0. Surface water sampling in the surface water streams on the western portion of the site
indicated non-detectable concentrations of PFAS. Conversely, some low detections of PFAS were reported
in the surface water sample collected on the northern side of the runway.
Given the remote location, the domestic (and all other use) water supply is drawn from bore water at the
Base. Sampling of the extracted bore water was completed as part of this PSI of both pre and post treated
water. The two samples collected did not detect concentrations of PFAS compounds above the laboratory
detection limit of 0.002 µg/L compared with the adopted drinking water criteria of 0.07 µg/L for PFOS/PFHxS.
On-property, bottled water is currently being supplied for drinking water purposes. Off-property, domestic
water supply is provided from either bore and/or surface water at the nearby Peppin residential camp which
is intermittently occupied. The source of water supply at the mining site could not be confirmed, but is likely
to include use of groundwater given the presence of registered bores onsite and the lack of reticulated water
in this locality.
During the reporting timeframe, Defence adjusted the scope of work to remove the re-categorisation task as
it was no longer required as part of the on-going Defence PFAS Program development.
12.2 Recommendations
Further investigation is recommended to progress the understanding of the contamination Conceptual Site
Model and the consequential assessment of potential risk. In developing the scope of work for a further
investigation, consideration of the data gaps identified in Section 11.5 is recommended.
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2 41
In addition, a program of periodic monitoring of the domestic water supply at the extraction bores (pre-
treatment) and water treatment plant (post treatment) is recommended. This recommendation is made to
provide lines of evidence that the water supply is suitable for use.
It is recommended that the design of a groundwater monitoring program consider the following:
Review of existing information of the set-up and operation groundwater extraction system. The purpose
of the review is to enable an informed understanding of zone of groundwater influence through the
operation of the system. Consideration of the depth that groundwater is extracted for the water supply,
and the potential zone of influence from bore pumping could be evaluated to further assess the
suitability of the water supply.
Monitoring be undertaken on a quarterly basis for an initial period of one year. Then review the
frequency and extent of this monitoring once data has been evaluated.
. The sampling of the water supply bores is recommended to be completed at the lowest commercially
available analytical reporting limit such that there is the maximum concentration range between this
analytical reporting limit and the adopted drinking water criteria. As such, if concentrations are reported
in future monitoring (but below the adopted criteria), there is an opportunity to ensure mitigations are in
place to avoid consumption of impacted water.
13.0 IMPORTANT INFORMATION
Your attention is drawn to the document Important Information Relating to this Report, which is included in
Appendix J of this report. The statements presented in this document are intended to advise you of what
your realistic expectations of this report should be, and to present you with recommendations on how to
minimise the risks associated with the services provided for this project. The document is not intended to
reduce the level of responsibility accepted by Golder Associates, but rather to ensure that all parties who
may rely on this report are aware of the responsibilities each assumes in so doing.
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2 42
14.0 REFERENCES
Defence 2016, Defence Contamination Directive (DCD) #8, (Amendment 1) – Interim Screening
Criteria. Defence Project Guidance for Per- and Poly-Fluoroalkyl Substances (PFAS). Department of
Defence, Estate and Infrastructure Group, September 2016.
Defence 2017, Defence Contamination Directive (DCD) #8, (Amendment 2) – Interim Screening
Criteria. Defence Project Guidance for Per- and Poly-Fluoroalkyl Substances (PFAS). Department of
Defence, Estate and Infrastructure Group, May 2017.
Department of the Environment and Energy, 2016. Commonwealth Environmental Management
Guidelines on Perfluorooctane Sulfonic Acid (PFOS) and Perfluorooctanoic Acid (PFOA). Draft. October
2016.
Department of Environment and Heritage Protection (QLD) (2009) Queensland Water Quality
Guidelines, Version 3, updated July 2013
Department of Natural Resources and Mines, Groundwater Database
ENSR – AECOM 2009 RAAF Base Scherger Environmental Monitoring Program for Water Quality
(NQ1998), draft, reference: App A_RAAFSGR EMP (WQ), dated May 2009
Jacobs 2016 – North Queensland Water Quality Monitoring, Department of Defence, RAAF Scherger
Groundwater Monitoring Report, Post Dry Season (IH074100-RBS_GW_Rd1_V1/1), dated 1
September 2016
Jacobs 2016 – North Queensland Water Quality Monitoring, Department of Defence, RAAF Scherger
Groundwater Monitoring Report, Post Wet Season (IH074100-RBS_GW_Rd1_V1/1), dated 1
September 2016
Jacobs 2016 – North Queensland Water Quality Monitoring, Department of Defence, RAAF Scherger
Surface Water Monitoring Report (IH074100-RBS_SW_V1/1) dated 1 September 2016
GHD 1989 Australian Construction Services, Cape York Airfield Environmental Assessment Phase,
Report on Groundwater Investigation, Report WS1, March 1989
GHD 1998 “RAAF Base Scherger at Peppan4 Cape York Peninsula Environmental Management Plan”
GHD 2001 – Environmental Works, North Queensland, Technical Report on RAAF Scherger
Environmental Monitoring (reference 42\10211\00- 46073, September 2001, GHD)
GHD 2002 – Corporate Services and Infrastructure Centre – North Queensland and Asset Services,
NQ1171 Far North Queensland Groundwater Monitoring Works – CMC Cairns Region, Report on
RAAF Base Scherger Groundwater Monitoring Report, (Reference: document No. 55512, Job No.
42/10868), dated 28 February 2002
Environmental Works, North Queensland, Technical Report on RAAF Scherger Environmental
Monitoring (reference 42\10211\00- 46073, September 2001, GHD)
Golder 2013 – Environmental Investigation of USTs/ASTs Across the Defence Estate, Stage 1 & 2
Report – RAAF Base Scherger (117623107-157) (May 2013, Golder Associates)
Golder 2016 – PFAS Environmental Management Program: Category 2 Property Data Gap Assessment
– RAAF Base Scherger (1541479-040) (September 2016, Golder Associates)
Golder 2017 – RAAF Base Scherger (1218) Sampling, Analysis and Quality Plan (Golder Ref 1652034-
059-R-Rev0, dated 13 April 2017).
4 Peppan used interchangeably with Peppin
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2 43
Mansell/AECOM 2005 – NQ01150 – Groundwater Monitoring Well Installation, Sample Capture and
Monitoring Report, RAAF Base Scherger AVTUR Fuel Farm (2004/2005) (reference 80200705, August
2005, Maunsell/AECOM)
National Environment Protection Council National Environment Protection (Assessment of Site
Contamination) Measure 1999 (as amended May 2013).
National Health and Medical Research Council (NHMRC) and Natural Resource Management
Ministerial Council (NRMMC) (2011) Australian Drinking Water Guidelines Paper 6 National Water
Quality Management Strategy, Version 3.3, updated November 2016
US EPA 2005. USEPA Hazard Assessment of PFOA and PFOS.
US EPA 2008. USEPA Contract Laboratory Program National Functional Guidelines for Superfund
Organic Methods Data Review.
US EPA 2010. USEPA Contract Laboratory Program National Functional Guidelines for Superfund
Inorganic Data Review.
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2 44
Report Signature Page
GOLDER ASSOCIATES PTY LTD
Andrew Holloway Francene Mitchell
Principal Scientist Principal Engineer
EC&FMM/AH
A.B.N. 64 006 107 857
Golder, Golder Associates and the GA globe design are trademarks of Golder Associates Corporation.
j:\contam\2016\1669283 defence psi cat 2\correspondence out\1669283_003_rev2_psi_scherger\1669283-003-r-rev2-psi report scherger.docx
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
FIGURES
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
TABLES
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX A AFFF Summary
PSI – RAAF BASE SCHERGER
Project No. 1669283-003-R-Rev1 1
Appendix A Table 1: Summary of AFFF Storage, Use and Waste Disposal
Location Product Storage Use / Purpose Waste Disposal Incidents / Training Remediation
2005 Exercise Training Areas (unknown locations)
Fire trucks parked at Building 7 fire station during the exercise.
Building 707
3M Lightwater and / or Ansulite used during 2005 exercise.
AFFF stored in mobile equipment including fire trucks utilised during the 2005 exercise.
It is understood that a fire truck with foam capability was stored at RAAF Scherger prior to and after the 2005 exercise in Building 707
Training exercise for emergency fire response. Site staff had no first-hand knowledge of the amount of AFFF that may have been sprayed during the 2005 training exercise.
No information reported by Defence during interview.
The 2005 training exercise involved having full fire emergency training drills due to the presence of the F111 aircraft. Fire trucks were stationed at Building 7 during the exercise when not operational. The location where trucks would have sprayed foam during the 2005 exercise is not known, but it was reported that it may have included the taxiways, various Ordnance Loading Areas (OLAs) and General Purpose Apron (GPA).
None
Ordnance Loading Areas (OLAs), General Purpose Apron (GPA), Marine Hangers
3M Lightwater historically.
Ansulite currently
At the time of Base commissioning, it was intended that there would be 1 x 50 litre foam fire extinguisher at each of the following locations, totalling 15 extinguishers: OLAs (10), Marine Hangers (2) and the General Purpose Apron (3).
Extinguishers positioned here for Base preparedness in case of fire emergency.
Fire extinguishers were serviced annually and involved purging of the waste AFFF onto the ground at each storage location (i.e. OLAs, Marine Hangers and GPA).
The site personnel were not aware of fire incidents or fire training using the extinguishers were reported.
None
Ordnance Loading Area (OLA) 3
and
Ordnance Loading Area (OLA) 8
Ansulite Centralised locations for storage of all 15 x 50 L mobile extinguishers
Extinguishers positioned here for Base preparedness in case of fire emergency.
Centralised location chosen for avoid deterioration of extinguishers in extreme weather and access to maintenance.
During extinguisher maintenance, waste AFFF was historically purged and discharged onto ground surface at either OLA3 or OLA8
Historical waste disposal involved discharge of AFFF to ground during extinguisher maintenance.
None, however it is understood that some of the pavement surface at OLA3 was resurfaced as part of asset maintenance.
PSI – RAAF BASE SCHERGER
Project No. 1669283-003-R-Rev1 2
Location Product Storage Use / Purpose Waste Disposal Incidents / Training Remediation
Ordnance Loading Area (OLA) 8
Ansulite 1000 L bulk container (IBC) at time of inspection
15 x 50 L mobile fire extinguisher present at time of site inspection in 2016. 3 currently in service, 12 awaiting hydrostatic testing.
1 x 20 L drum foam (Solberg) at time of inspection
1000 L IBC stored here containing waste AFFF from servicing / purging of mobile fire extinguishers.
50 L mobile fire extinguishers either serviced at OLA8 or taken off Base and replaced with serviced extinguishers. Onsite servicing involved purging of AFFF into IBC.
1 x 20 L foam drum understood to be available for use with water fire truck in the event of emergency.
From approximately 2014, waste disposal practices of AFFF during extinguisher maintenance was changed. Waste AFFF was temporarily stored onsite in IBC.
IBC consequently transported offsite for appropriate disposal by Chubb.
No incidents identified, other than routine waste disposal as part of extinguisher servicing.
No fire training known to have occurred here.
None
General Purpose Apron
As above for historical activities at GPA.
At time of inspection, it was noted that 1 x 50L mobile fire extinguisher (Ansulite) was present.
1 x 50 L mobile fire extinguisher.
Extinguishers positioned here for Base preparedness in case of fire emergency
Historical waste disposal (both 3M Lightwater and Ansulite) from servicing of fire extinguishers understood to have occurred at GPA.
No incidents identified, other than routine waste disposal as part of extinguisher servicing.
No fire training known to have occurred here.
None
PSI – RAAF BASE SCHERGER
Project No. 1669283-003-R-Rev1 3
Location Product Storage Use / Purpose Waste Disposal Incidents / Training Remediation
Building 707 Warehouse
3M Lightwater (historical) / Ansulite – stored in fire truck historically parked in this Warehouse. Foam capability fire truck has been removed from Base and replaced with water-capability truck.
Ansulite stored in IBC associated with Lewie Fire servicing extinguisher program.
Since 2014, Lewie Fire has used this warehouse for the servicing of their contracted fire extinguishers. It is noted that Chubb Fire service other extinguishers.
Previously foam fire truck parked in this warehouse.
1000 L IBC stored here containing waste AFFF from servicing/ purging of mobile fire extinguishers.
Fire extinguishers are serviced annually and involve purging of the waste AFFF into IBC. Alternately, waste extinguishers are removed offsite and replaced with new extinguishers.
No anecdotal reports of fire incidents or fire training using the extinguishers were reported.
No anecdotal reports
Vehicle Refuelling - Building 701
and
Underground Storage Tank (UST) Fuel Installation
and
Fuel Tanker Refuelling Bay
Historically 3MLightwater
Ansulite
A number of 10L mobile fire extinguishers are positioned at each of the fuel storage and distribution points at these facilities.
Extinguishers positioned here for Base preparedness in case of fire emergency.
Serviced centrally in Warehouse 707 or alternately old extinguishers replaced with new.
No anecdotal reports of fire incidents or fire training using the extinguishers were reported.
No anecdotal reports.
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX B Photographs
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 1/14
Location: W002 Date: 4/05/2017
Direction: North west Comment: Post water treatment plant
Location: W001 Date: 4/05/2017
Direction: South Comment: Pre water treatment plant
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 2/14
Location: SW001/SD001 Date: 4/05/2017
Direction: North Comment: No surface water collected. Located near OLA3.
Location: SW002/SD002 Date: 5/05/2017
Direction: North Comment: No surface water collected. Located near OLA8.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 3/14
Location: SW004/SD004 Date: 4/05/2017
Direction: North west Comment: No surface water collected. Located near
Building #7
Location: S003/SD003 Date: 4/05/2017
Direction: South Comment: No surface water collected. Located near the
General Purpose Apron.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 4/14
Location: SW005/SD005 Date: 4/05/2017
Direction: North west Comment: No surface water collected.
Location: SW006/SD006 Date: 5/05/2017
Direction: North west Comment: Deep animal wallow filled with water in
foreground. Along west boundary.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 5/14
Location: SW007/SD007 Date: 5/05/2017
Direction: South west Comment: Under road culvert with shallow concrete
platform. Sample taken from deeper natural area
in background.
Location: SW008/SD008 Date: 5/05/2017
Direction: North Comment: Surface water not collected. Located north of the
Sewage Treatment Plant.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 6/14
Location: SW009/SD009 Date: 5/05/2017
Direction: North east Comment: Surface water flowing through road gravels
offsite to the west.
Location: SW010/SD010 Date: 5/05/2017
Direction: North east Comment: West of the General Purpose Apron.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 7/14
Location: SW011/SD011 Date: 5/05/2017
Direction: North east Comment: Surface water flowing across road offsite to the
west.
Location: SW012/SD012 Date: 5/05/2017
Direction: South Comment: Surface water flowing south west offsite
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 8/14
Location: SW013/SD013 Date: 9/05/2017
Direction: South Comment: Located along north east boundary road.
Location: IDW Stockpile Date: 13/05/2017
Direction: North east Comment: Drilling spoil. Three samples obtained from
stockpile (IDW01, IDW02, IDW03)
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 9/14
Location: IDW Stockpile Date: 13/05/2017
Direction: South east Comment: Drilling spoil. Three samples obtained from
stockpile (IDW01, IDW02, IDW03)
Location: RAAFSGR10 Date: 16/05/2017
Direction: South west Comment: Located across the road from the Aviation Fuel
Farm.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 10/14
Location: RAAFSGR14 Date: 16/05/2017
Direction: North west Comment: Located near the Central Power Station.
Location: RAAFSGR18 Date: 16/05/2017
Direction: North Comment: Motor Transport Facility
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 11/14
Location: RAAFSGR19 Date: 16/05/2017
Direction: North Comment: Motor Transport Facility
Location: BH022 Date: 2/05/2017
Direction: South east Comment: Located next to General Purpose Apron.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 12/14
Location: BH023 Date: 10/05/2017
Direction: East Comment: Located across from Building #7.
Location: BH024 Date: 2/05/2017
Direction: West Comment: Located near OLA8.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 13/14
Location: BH025 Date: 2/05/2017
Direction: South Comment: Located near OLA3.
Location: BH026 Date: 9/05/2017
Direction: West Comment: Road leading to the Sewage Treatment Plant.
APPENDIX B Photograph Log
27 July 2017 Project No. 1669283-003-R-Rev1 14/14
Location: BH027 Date: 8/05/2017
Direction: North west Comment: Along the north west boundary fence.
\\golder.gds\gap\brisbane\jobs\contam\2016\1669283 defence psi cat 2\correspondence out\1669283_003_rev1_psi_scherger\b photos\app b photograph log rev1.docx
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX C Aerial photographs
1969 AERIAL VIEW OF THE SITE
SITE
1988 AERIAL VIEW OF THE SITE
SITE
1990 AERIAL VIEW OF THE SITE
SITE
1993 AERIAL VIEW OF THE SITE
SITE
1996 AERIAL VIEW OF THE SITE
SITE
1999 AERIAL VIEW OF THE SITE
SITE
2005 AERIAL VIEW OF THE SITE
SITE
2013 AERIAL VIEW OF THE SITE
SITE
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX D Topographic Map and Identified Natural Springs
Excerpt from GHD report (2002) Corporate Services and Infrastructure Centre – North Queensland and Asset Services, NQ1171 Far North Queensland Groundwater Monitoring Works – CMC Cairns Region, Report on RAAF Base Scherger Groundwater Monitoring. (Reference: document No. 55512, Job No. 42/10868), dated 28 February 2002
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX E Registered bore search
Registered Groundwater Bore Search – RAAF Base Scherger
Source: Queensland
Department of Natural
Resources and Mines (June
2017)
RN99245
RN99253
RN99282
RN99283 RN78995
RN92284
RN109173
RN78994RN78863
RN78862
RN92285 RN92286
RN157560
RN157558
RN157559
RN157556
RN157557
RN157568
RN157569
RN157561
RN157562
RN157563
RN157564
RN157566
RN157576
RN157565
On‐site record
Off‐site record
RN92281
RN99254
RN45271
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-51LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-05-28LONGITUDE MAP-SERIES
5032D/O FILE NO.
SHIRE 618501EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601606NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.64742364GIS LAT142.091189097GIS LNG
4957-WEIPAPARISH NAME
WEIPACOUNTY
BORE NO 2ORIGINAL BORE NO
-BORE LINE
DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
AQUIFER DETAILS
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
M
254
Mareeba
REGISTRATION DETAILS
9241
422
RP859798
RAAF BASE WEIPA
2500-COOK
78863REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A A
PIPE
31/05/1993 07/06/1993 16/06/199321/06/1993 26/07/1993 02/08/199311/08/1993 17/08/1993 23/08/199330/08/1993 06/09/1993 14/09/199330/09/1993 04/10/1993 14/10/199318/10/1993 25/10/1993 02/11/199308/11/1993 15/11/1993 17/11/199322/11/1993 31/01/1994 10/02/199422/03/1994 28/03/1994 20/04/199430/04/1994 15/05/1994 24/05/199406/06/1994 17/06/1994 26/06/199410/07/1994 19/07/1994 31/07/199408/08/1994 17/08/1994 24/08/199430/08/1994 07/09/1994 23/09/199405/10/1994 12/10/1994 27/10/199402/11/1994 07/12/1994 31/01/199516/02/1995 24/02/1995 17/03/199524/03/1995 01/04/1995 19/04/199528/04/1995 26/05/1995 31/05/199519/06/1995 01/07/1995 13/07/1995
DATE
-6.00 -6.20 -6.60-6.60 -7.60 -7.60-7.70 -7.70 -8.00-8.20 -8.40 -8.20-8.60 -8.60 -9.50-8.90 -9.00 -9.20-9.40 -9.20 -9.30-9.40 -8.80 -8.70-5.83 -5.83 -5.82-6.17 -6.45 -6.87-7.26 -7.50 -7.66-8.20 -8.20 -8.69-8.70 -8.58 -8.66-8.90 -9.18 -9.70-9.92 -10.02 -10.15-10.35 -9.70 -8.80-9.20 -8.80 -5.68-5.48 -5.82 -5.41-5.62 -6.41 -6.58-7.02 -7.36 -7.89
MEASURE(m)
R R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R R
N/R RMK
A
PIPE
31/05/1993
DATE
40.55
ELEVATION
AHD
DATUM
SVY
PRECISION
R
MEASUREMENT POINT
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
BORE CONDITION
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
78863REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
RAAF
SURVEY SOURCE
NR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NR
MEASTYPE
MEASTYPE
MEASTYPE
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A AA A A
PIPE
26/07/1995 11/08/1995 21/08/199531/08/1995 18/09/1995 30/09/1995
DATE
-8.25 -8.36 -9.04-9.11 -9.69 -10.09
MEASURE(m)
R R RR R R
N/R RMK
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
SPECIAL WATER ANALYSIS
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
78863REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
NR NR NRNR NR NR
MEASTYPE
MEASTYPE
MEASTYPE
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
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Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:47:36 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-57LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-05-34LONGITUDE MAP-SERIES
5032D/O FILE NO.
SHIRE 618662EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601425NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.649061017GIS LAT142.092677684GIS LNG
4957-WEIPAPARISH NAME
WEIPACOUNTY
BORE NO 1ORIGINAL BORE NO
-BORE LINE
DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
AQUIFER DETAILS
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
M
254
Mareeba
REGISTRATION DETAILS
9241
422
RP859798
RAAF BASE WEIPA
2500-COOK
78862REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
AA
PIPE
15/09/199315/09/1993
DATE
12
RD
01155704
QAN DEPTH
(m)PUPU
RMK
GBGB
SRC
11092
COND(uS/cm)
5.05.9
pH
8
Si(mg/L)
48.86
TOTALIONS
(mg/L)
54.14
TOTALSOLIDS
(mg/L)
2
HARD
4
ALK
0.3
FIG. OFMERIT
1.0
SAR
0.04
RAH
A
A
PIPE15/09/1993
15/09/1993
DATE1
2
RD
3.1
Na
19.6
K
0.3
Ca
0.3
Mg
0.01
Mn
5.0
HCO3
0.00
Fe
0.0
CO3
20.5
Cl
0.00
F
0.1
NO3
0.0
SO4 Zn Al B Cu
A A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A A
PIPE
31/05/1993 07/06/1993 16/06/199321/06/1993 05/07/1993 13/07/199319/07/1993 20/07/1993 22/07/199326/07/1993 02/08/1993 11/08/199317/08/1993 23/08/1993 30/08/199306/09/1993 14/09/1993 30/09/199304/10/1993 14/10/1993 18/10/199325/10/1993 02/11/1993 08/11/199315/11/1993 17/11/1993 22/11/199310/02/1994 17/02/1994 28/02/199422/03/1994 28/03/1994 20/04/199430/04/1994 15/05/1994 24/05/199406/06/1994 17/06/1994 26/06/199410/07/1994 19/07/1994 31/07/199408/08/1994
DATE
-6.40 -6.50 -6.80-7.00 -7.30 -7.50-7.30 -7.50 -7.40-7.80 -8.00 -8.20-8.00 -8.30 -8.40-8.60 -8.60 -9.00-9.00 -9.20 -9.30-9.30 -9.50 -9.50-9.50 -9.50 -9.50-9.05 -8.70 -8.40-6.30 -5.93 -5.83-6.27 -6.53 -6.75-7.42 -7.55 -7.70-8.25 -8.90 -8.59
MEASURE(m)
R R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR
N/R RMK
A
PIPE
31/05/1993
DATE
41.11
ELEVATION
AHD
DATUM
SVY
PRECISION
R
MEASUREMENT POINT
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
BORE CONDITION
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
DNRGCL
ANALYST
78862REG NUMBER
**** NO RECORDS FOUND ****
RAAF
SURVEY SOURCE
NR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR
MEASTYPE
MEASTYPE
MEASTYPE
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A A A
PIPE
17/08/1994 24/08/199430/08/1994
DATE
-8.64 -8.70 -8.96-9.00
MEASURE(m)
R RR
N/R RMK
A
PIPE
15/09/1993
DATE DEPTH(m)
110
COND(uS/cm)
pH TEMP(C)
NO3(mg/L)
DO(mg/L)
Eh(mV)
PU
METH
GB
SOURCE
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
SPECIAL WATER ANALYSIS
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
78862REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
NR NRNR
MEASTYPE
MEASTYPE
MEASTYPE
ALK(mEq)
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:47:57 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-43LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-04-24LONGITUDE MAP-SERIES
515/0003119D/O FILE NO.
SHIRE 616552EASTING MAP-NO
R/O FILE NO.
LOT 8600000NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
100GPS ACC
PRES EQUIPMENT
YCHECKED
-12.661819244GIS LAT142.073430938GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
PEPPINORIGINAL BORE NO
-BORE LINE
11/11/1999DATE DRILLED
POLYGON
DELAI, MARK ANDREWDRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYROTARY MUDMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSWSROLES
A
A
A
A
A
A
PIPE
11/11/1999
11/11/1999
11/11/1999
11/11/1999
11/11/1999
11/11/1999
DATE
1
2
3
4
5
6
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
7.200
2.000
2.000
5.000
MAT SIZE(mm)
WT
AP
AP
GR
SIZE DESC
140
140
140
200
200
200
OUTSIDEDIAM(mm)
0.00
4.00
24.00
4.00
3.50
0.00
TOP(m)
30.00
8.00
30.00
30.00
4.00
3.50
BOTTOM(m)
1
2
3
RECORDNUMBER
0.00
3.00
4.00
STRATATOP (m)
3.00
4.00
8.00
STRATABOT (m)
BAUXITE
IRONSTONE CEMENTED BAUXITE
SAND *
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9241
7024
MP41159
2500-COOK
109173REG NUMBER
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
REC
4.00
23.00
TOPBED(M)
8.00
30.00
BOTTOMBED(M)
BEDLITHOLOGY
11/11/1999
DATE
-6.30
SWL(m)
N
N
FLOW QUALITY
SAND
MDST
0.10
0.10
YIELD(l/s)
Y
Y
CTR
UC
FR
CONDIT FORMATION NAME
4
5
6
7
8
9
10
11
RECORDNUMBER
8.00
9.00
12.00
16.00
23.00
STRATATOP (m)
9.00
12.00
16.00
23.00
30.00
STRATABOT (m)
SANDY CLAY
WHITE KAOLIN CLAY
WHITE AND BROWN CLAY
BROWN SHALEY CLAY
MUDSTONE *
AIRTEST AT 0.2 L/S
SWL 16/11/1999 -6.3M BGL
DRILLER - M.DELAI
STRATA DESCRIPTION
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
109173REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A X
PIPE
16/11/1999 16/11/1999
DATE
-7.20 -6.30
MEASURE(m)
R N
N/R RMK
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
SPECIAL WATER ANALYSIS
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
109173REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
NR NR
MEASTYPE
MEASTYPE
MEASTYPE
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:49:37 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-54LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-04LONGITUDE MAP-SERIES
D/O FILE NO.
SHIRE 619568EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601503NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.648316735GIS LAT142.101013485GIS LNG
4957-WEIPAPARISH NAME
WEIPACOUNTY
COMALCO NO.23ORIGINAL BORE NO
-BORE LINE
11/08/1970DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
1
2
3
4
5
6
7
8
9
10
11
RECORDNUMBER
0.00
0.61
2.29
3.66
STRATATOP (m)
0.61
2.29
3.66
7.62
STRATABOT (m)
SILTY CLAY: FIRM, DRY, DARK BROWN;
OF MEDIUM PLASTICITY
BAUXITE GRAVEL: MEDIUM DENSE,
POORLY GRADED; WITH A TRACE OF ORANGE
-BROWN, SILTY CLAY
IRONSTONE AND BAUXITE GRAVEL: MEDIUM
DENSE, POORLY SORTED GRADED; WITH
A TRACE OF ORANGE-BROWN, SILTY CLAY
SANDY CLAY: STIFF, YELLOW, YELLOW-
BROWN AND WHITE MOTTLED, KAOLINITIC;
OF MEDIUM TO HIGH PLASTICITY; WITH
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
M
254
Mareeba
REGISTRATION DETAILS
9241
422
RP859798
2500-COOK
92285REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
DNR
DNR
SOURCE
1
2
RECORDNUMBER
0.00
3.70
STRATATOP (m)
3.70
13.20
STRATABOT (m)
BULIMBA FORMATION
BULIMBA FORMATION
STRATA DESCRIPTION
12
13
14
15
16
17
18
19
20
21
22
23
24
25
RECORDNUMBER
7.62
9.45
13.11
STRATATOP (m)
9.45
13.11
13.21
13.21
STRATABOT (m)
SOME SILT SAND IS MEDIUM TO FINE
GRAINED, QUARTZOSE
SAND: MEDIUM DENSE, POORLY GRADED,
MEDIUM TO FINE GRAINED, ANGULAR,
FERRUGINOUSLY-STAINED, QUARTZOSE
SAND: AS FOR (7.62 - 9.45M)
EXCEPT NO STAINING
SILTY CLAY: STIFF, WHITE, KAOLINITIC
OF MEDIUM TO HIGH PLASTICITY
*********** TOTAL DEPTH *************
REFER TO: COFFEY & HOLLINGSWORTH,
1971 - SHALLOW AQUIFER INVESTIGATION
WEIPA, NORTH QLD. REP. TO COMALCO
LTD (UNPUBL.)
STRATA DESCRIPTION
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
92285REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
SPECIAL WATER ANALYSIS
92285REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:47:13 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-55LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-04-04LONGITUDE MAP-SERIES
D/O FILE NO.
SHIRE 615963EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601502NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.648465676GIS LAT142.067819195GIS LNG
4957-WEIPAPARISH NAME
WEIPACOUNTY
COMALCO NO.22ORIGINAL BORE NO
-BORE LINE
10/08/1970DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
1
2
3
4
5
6
7
8
9
10
11
RECORDNUMBER
0.00
0.23
0.84
1.75
STRATATOP (m)
0.23
0.84
1.75
2.90
STRATABOT (m)
SILTY CLAY: FIRM, DRY, BROWN; OF
MEDIUM PLASTICITY
SILTY CLAY: AS FOR (0 -0.23M), BUT
ORANGE BROWN; WITH SOME FINE
GRAINED, ROUNDED BAUXITE GRAVEL
BAUXITE GRAVEL: MEDIUM DENSE, POORLY
GRADED, SUB-ROUNDED TO ROUNDED; WITH
SOME ORANGE-BROWN; SILTY CLAY
BAUXITE GRAVELLY SAND: MEDIUM DENSE,
POORLY GRADED, ROUNDED; WITH SOME
FINE GRAINED, SUB-ANGULAR, IRONSTONE
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
M
254
Mareeba
REGISTRATION DETAILS
9241
422
RP859798
2500-COOK
92284REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
DNR
DNR
SOURCE
1
2
RECORDNUMBER
0.00
4.80
STRATATOP (m)
4.80
10.40
STRATABOT (m)
BULIMBA FORMATION
BULIMBA FORMATION
STRATA DESCRIPTION
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
RECORDNUMBER
2.90
4.80
7.82
10.26
STRATATOP (m)
4.80
7.82
10.26
10.41
10.41
STRATABOT (m)
GRAVEL AND A TRACE OF ORANGE-BROWN,
SILTY CLAY
IRONSTONE GRAVEL: DENSE, POORLY
GRADED; WITH SOME YELLOW, SILTY CLAY
OF MEDIUM TO HIGH PLASTICITY
SAND: MEDIUM DENSE, WELL GRADED,
ANGULAR, QUARTZOSE; WITH SOME FINE
GRAINED IRONSTONE GRAVEL AND A TRACE
OF WHITE, SILTY CLAY
GRAVELLY SAND: MEDIUM DENSE, WELL
GRADED, ANGULAR; WITH SOME WHITE,
KAOLINITIC, SILTY OF MEDIUM TO
HIGH PLASTICITY
SILTY CLAY: STIFF, WHITE, MOTTLED
WITH YELLOW-BROWN, KAOLINITIC; OF
MEDIUM TO HIGH PLASTICITY
*********** TOTAL DEPTH *************
REFER TO: COFFEY & HOLLINGSWORTH,
1971 - SHALLOW AQUIFER INVESTIGATION
WEIPA, NORTH QLD. REP. TO COMALCO
LTD (UNPUBL.)
STRATA DESCRIPTION
AQUIFER DETAILS
STRATIGRAPHY DETAILS
92284REG NUMBER
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
92284REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:49:09 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-37LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-04-12LONGITUDE MAP-SERIES
5032D/O FILE NO.
SHIRE 616207EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8602044NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
NEPRES EQUIPMENT
YCHECKED
-12.643553512GIS LAT142.070052048GIS LNG
4957-WEIPAPARISH NAME
WEIPACOUNTY
BORE NO. 4ORIGINAL BORE NO
-BORE LINE
DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
AQUIFER DETAILS
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
M
254
Mareeba
REGISTRATION DETAILS
9241
422
RP859798
RAAF BASE WEIPA
2500-COOK
78995REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A A
PIPE
30/09/1993 04/10/1993 14/10/199318/10/1993 25/10/1993 02/11/199308/11/1993 15/11/1993 17/11/199322/11/1993 31/01/1994 10/02/199417/02/1994 28/02/1994 22/03/199428/03/1994 20/04/1994 30/04/199415/05/1994 24/05/1994 06/06/199417/06/1994 20/06/1994 26/06/199410/07/1994 19/07/1994 31/07/199408/08/1994 17/08/1994 24/08/199407/09/1994 23/09/1994 05/10/199412/10/1994 07/12/1994 31/01/199516/02/1995 24/02/1995 17/03/199524/03/1995 01/04/1995 19/04/199528/04/1995 26/05/1995 31/05/199519/06/1995 01/07/1995 13/07/199526/07/1995 11/08/1995 21/08/199531/08/1995 18/09/1995 30/09/1995
DATE
-8.90 -9.10 -9.30-9.40 -9.50 -9.60-9.60 -9.50 -9.60-9.70 -5.85 -6.10-5.90 -5.50 -4.76-5.23 -5.53 -5.66-5.45 -5.73 -5.90-5.85 -5.85 -5.70-5.80 -5.90 -4.11-5.90 -5.89 -5.90-4.00 -4.10 -4.40-4.55 -7.60 -5.65-5.55 -5.60 -4.30-4.53 -5.08 -5.28-5.35 -5.52 -5.50-5.57 -5.59 -5.58-5.62 -5.63 -5.61-5.73 -5.80 -5.89
MEASURE(m)
R R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R R
N/R RMK
AX
PIPE
31/05/199231/05/1992
DATE
25.5024.50
ELEVATION
AHDAHD
DATUM
SVYEST
PRECISION
RN
MEASUREMENT POINT
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
BORE CONDITION
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
78995REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
RAAF
SURVEY SOURCE
NR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NR
MEASTYPE
MEASTYPE
MEASTYPE
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
SPECIAL WATER ANALYSIS
78995REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:48:26 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-46LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-05-41LONGITUDE MAP-SERIES
5032D/O FILE NO.
SHIRE 618890EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601769NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
NEPRES EQUIPMENT
YCHECKED
-12.645935087GIS LAT142.094761608GIS LNG
4957-WEIPAPARISH NAME
WEIPACOUNTY
BORE NO. 3ORIGINAL BORE NO
-BORE LINE
DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
AQUIFER DETAILS
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
M
254
Mareeba
REGISTRATION DETAILS
9241
422
RP859798
RAAF BASE WEIPA
2500-COOK
78994REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA A AA
PIPE
04/10/1993 14/10/1993 18/10/199325/10/1993 02/11/1993 08/11/199315/11/1993 17/11/1993 22/11/199331/01/1994 10/02/1994 17/02/199428/02/1994 22/03/1994 28/03/199420/04/1994 30/04/1994 15/05/199424/05/1994 06/06/1994 17/06/199420/06/1994 26/06/1994 10/07/199419/07/1994 31/07/1994 08/08/199417/08/1994 24/08/1994 07/09/199423/09/1994 05/10/1994 12/10/199427/10/1994 02/11/1994 07/12/199431/01/1995 16/02/1995 24/02/199517/03/1995 24/03/1995 01/04/199519/04/1995 28/04/1995 26/05/199531/05/1995 19/06/1995 01/07/199513/07/1995 26/07/1995 11/08/199521/08/1995 31/08/1995 18/09/199530/09/1995
DATE
-9.00 -9.10 -9.30-9.50 -9.80 -9.90-10.00 -9.80 -10.10-10.30 -9.00 -8.40-6.70 -4.83 -5.26-5.58 -6.15 -6.10-6.63 -6.59 -7.32-7.32 -7.68 -8.10-8.28 -8.70 -8.77-8.85 -8.94 -9.22-9.44 -9.75 -9.93-10.40 -10.45 -10.70-10.30 -10.15 -10.05-4.96 -4.91 -5.48-5.44 -5.70 -6.50-6.61 -9.16 -7.55-7.90 -8.27 -8.50-8.74 -8.93 -9.28-9.54
MEASURE(m)
R R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR R RR
N/R RMK
AX
PIPE
31/05/199231/05/1992
DATE
42.7441.74
ELEVATION
AHDAHD
DATUM
SVYEST
PRECISION
RN
MEASUREMENT POINT
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
BORE CONDITION
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
78994REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
RAAF
SURVEY SOURCE
NR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR NR NRNR
MEASTYPE
MEASTYPE
MEASTYPE
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
SPECIAL WATER ANALYSIS
78994REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:46:01 AM **
1Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-37-31LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-02-02LONGITUDE MAP-SERIES
463D/O FILE NO.
SHIRE 612278EASTING MD6601-A1MAP-NO
R/O FILE NO.
LOT 8604099NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
NEPRES EQUIPMENT
YCHECKED
-12.625116896GIS LAT142.033800223GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
SA 79ORIGINAL BORE NO
-BORE LINE
06/11/1962DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
A
A
PIPE
06/11/1962
06/11/1962
DATE
1
2
RECORDNUMBER
Steel Casing
Screen
MATERIAL DESCRIPTION MAT SIZE(mm)
SIZE DESC
50
50
OUTSIDEDIAM(mm)
0.00
TOP(m)
14.00
BOTTOM(m)
1
2
3
4
5
6
7
RECORDNUMBER
0.00
0.38
3.96
5.18
6.10
12.19
STRATATOP (m)
0.38
3.96
5.18
6.10
12.19
14.02
STRATABOT (m)
OVERBURDEN
RED SANDY CLAY
RED SANDY CLAY & IRONSTONE
RED & YELLOW CLAY,SOME COARSE & OLD
QUARTZ PEBBLES
CLAY & IRONSTONE
RED & YELLOW CLAY
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
M
503
Mareeba
REGISTRATION DETAILS
9241
7024
MP41159
COMALCO
2500-COOK
99245REG NUMBER
DATA OWNER
DATE LOG RECD
2Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
DNR
DNR
DNR
SOURCE
1
2
3
RECORDNUMBER
0.00
0.40
14.00
STRATATOP (m)
0.40
14.00
30.20
STRATABOT (m)
SURFICIAL
BULIMBA FORMATION
ROLLING DOWNS GROUP
STRATA DESCRIPTION
8
9
10
11
12
13
14
15
16
17
18
RECORDNUMBER
14.02
24.38
STRATATOP (m)
24.38
30.18
STRATABOT (m)
BROWN SILTSTONE
GREY SILTSTONE
WATER CUT AT 22.7M UNDER HARD
MUDSTONE BAND
152MM HOLE DRILLED
18.09.1962 SWL -19.96M
ORIGINALLY OBSERVATION BORE NO 012
DRILLED BY COMALCO
COMMENCED 18.09.1962
COMPLETED 06.11.1962
NO OTHER DETAILS AVAILABLE
STRATA DESCRIPTION
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
99245REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A AA A AA A AA
PIPE
29/01/1976 31/03/1976 21/04/197623/06/1976 23/07/1976 24/09/197628/10/1976 30/11/1976 24/12/197625/02/1977
DATE
-8.15 -10.15 -10.84-11.64 -11.54 -11.86-12.05 -12.21 -12.18-8.38
MEASURE(m)
R R RR R RR R RR
N/R RMK
AX
PIPE
29/01/197629/01/1976
DATE
29.8529.24
ELEVATION
ASDASD
DATUM
SVYSVY
PRECISION
RN
MEASUREMENT POINT
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
SPECIAL WATER ANALYSIS
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
99245REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
SURVEY SOURCE
NR NR NRNR NR NRNR NR NRNR
MEASTYPE
MEASTYPE
MEASTYPE
4Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 20/06/2017 03:37:34 PM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-55LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-07-03LONGITUDE MAP-SERIES
D/O FILE NO.
SHIRE 621362EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601479NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.648465568GIS LAT142.117536169GIS LNG
4957-WEIPAPARISH NAME
WEIPACOUNTY
COMALCO NO.24ORIGINAL BORE NO
-BORE LINE
11/08/1970DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
1
2
3
4
5
6
7
8
9
10
11
RECORDNUMBER
0.00
0.38
2.80
STRATATOP (m)
0.38
2.80
3.12
STRATABOT (m)
SILTY CLAY: FIRM, DRY, DARK BROWN;
OF MEDIUM PLASTICITY; WITH SOME
MEDIUM TO FINE GRAINED, QUARTZOSE
SAND
CLAYEY SAND: STIFF, MOIST, MOTTLED
BROWN, KAOLINTIC; OF MEDIUM
PLASTICITY. SAND IS FAIRLY WELL
GRADED
SANDY CLAY: STIFF, YELLOW-BROWN,
KAOLINTIC, SILTY; OF MEDIUM TO HIGH
PLASTICITY
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
M
254
Mareeba
REGISTRATION DETAILS
9241
7024
MPH41159
2500-COOK
92286REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
DNR
SOURCE
1
RECORDNUMBER
0.00
STRATATOP (m)
3.10
STRATABOT (m)
BULIMBA FORMATION
STRATA DESCRIPTION
12
13
14
15
16
RECORDNUMBER
STRATATOP (m)
3.12
STRATABOT (m)
************ TOTAL DEPTH ************
REFER TO: COFFEY & HOLLINGSWORTH,
1971 - SHALLOW AQUIFER INVESTIGATION
WEIPA, NORTH QLD. REP TO COMALCO
LTD (UNPUBL.)
STRATA DESCRIPTION
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
92286REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
SPECIAL WATER ANALYSIS
92286REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:59:26 AM **
1Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-54LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-03-03LONGITUDE MAP-SERIES
D/O FILE NO.
SHIRE 614120EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601526NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.648316872GIS LAT142.050849903GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
COMALCO NO.21ORIGINAL BORE NO
-BORE LINE
10/08/1970DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
1
2
3
4
5
6
7
8
9
10
11
RECORDNUMBER
0.00
0.30
2.44
5.94
STRATATOP (m)
0.30
2.44
5.94
7.16
STRATABOT (m)
SILTY CLAY: FIRM, DRY, DARK GREY;
OF MEDIUM PLASTICITY
SILTY CLAY: FIRM, RED-BROWN; OF
MEDIUM PLASTICITY; WITH SOME
IRONSTONE AND BAUXITE GRAVEL
SAND: MEDIUM DENSE, FAIRLY WELL
GRADED, ANGULAR, FERRUGINOUSLY
STAINED, KAOLINITIC, SILTY CLAY
SILTY CLAY: STIFF, WHITE MOTTLED
WITH BROWN; OF MEDIUM TO HIGH
PLASTICITY
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
M
254
Mareeba
REGISTRATION DETAILS
9241
7024
MPH41159
2500-COOK
92283REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
DNR
DNR
SOURCE
1
2
RECORDNUMBER
0.00
5.90
STRATATOP (m)
5.90
7.20
STRATABOT (m)
BULIMBA FORMATION
BULIMBA FORMATION
STRATA DESCRIPTION
12
13
14
15
16
RECORDNUMBER
STRATATOP (m)
7.16
STRATABOT (m)
************ TOTAL DEPTH ************
REFER TO: COFFEY & HOLINGSWORTH,
1971 - SHALLOW AQUIFER INVESTIGATION
WEIPA, NORTH QLD. REP. TO COMALCO
LTD (UNPUBL.)
STRATA DESCRIPTION
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
92283REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
SPECIAL WATER ANALYSIS
92283REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 20/06/2017 03:52:15 PM **
1Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-55LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-03-03LONGITUDE MAP-SERIES
D/O FILE NO.
SHIRE 614112EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8599665NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.665137221GIS LAT142.050849831GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
COMALCO NO.19ORIGINAL BORE NO
-BORE LINE
07/08/1970DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
1
2
3
4
5
6
7
8
9
10
11
RECORDNUMBER
0.00
0.91
2.23
4.19
STRATATOP (m)
0.91
2.23
4.19
4.80
STRATABOT (m)
SILTY CLAY: SOFT, DARK GREY; OF
LOW PLASTICITY
GRAVELLY CLAY: FIRM, RED-BROWN;
OF MEDIUM PLASTICITY; GRAVEL BEING
MEDIUM TO FINE GRAINED IRONSTONE
SAND: MEDIUM DENSE, POORLY GRADED,
MEDIUM TO FINE GRAINED IRONSTONE
GRAVEL AND A TRACE OF YELLOW-BROWN,
SILTY CLAY
SAND: MEDIUM DENSE, MEDIUM TO COARSE
GRAINED, ANGULAR, QUARTZOSE; WITH
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
M
254
Mareeba
REGISTRATION DETAILS
9241
7024
MPH41159
2500-COOK
92281REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
DNR
DNR
SOURCE
1
2
RECORDNUMBER
0.00
4.20
STRATATOP (m)
4.20
6.10
STRATABOT (m)
BULIMBA FORMATION
BULIMBA FORMATION
STRATA DESCRIPTION
12
13
14
15
16
17
18
19
20
21
RECORDNUMBER
4.80
STRATATOP (m)
6.10
6.10
STRATABOT (m)
SOME YELLOW-BROWN, SILTY CLAY OF
MEDIUM PLASTICITY
SILTY CLAY: STIFF, YELLOW-BROWN,
MOTTLED WITH WHITE, KAOLINITIC; OF
MEDIUM TO HIGH PLASTICITY
*********** TOTOAL DEPTH ************
REFER TO: COFFEY & HOLLINGSWORTH,
1971 - SHALLOW AQUIFER INVESTIGATION
WEIPA, NORTH QLD. REP. TO COMALCO
LTD (UNPUBL.)
STRATA DESCRIPTION
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
92281REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
SPECIAL WATER ANALYSIS
92281REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 20/06/2017 03:54:23 PM **
1Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
BASIN 12-38-07LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-01-59LONGITUDE MAP-SERIES
4684D/O FILE NO.
SHIRE 612190EASTING MD6601-A1MAP-NO
R/O FILE NO.
LOT 8602989NORTHING MAP NAME
L36885BH/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.63515617GIS LAT142.033027795GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
SA 127ORIGINAL BORE NO
-BORE LINE
DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
1
2
3
4
5
RECORDNUMBER
STRATATOP (m)
STRATABOT (m)
OFFICE REGISTRATION ONLY
WATER LEVEL OBSERVATION BORE
DEPTH 16.0M
50MM CASING 0.0M - 16.0M
DRILLED BY COMALCO
STRATA DESCRIPTION
AQUIFER DETAILS
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
M
503
Mareeba
REGISTRATION DETAILS
9241
7024
MP41159
SBML 1 - WEIPA
2500-COOK
45271REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
45271REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 20/06/2017 03:47:34 PM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-24LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-07-41LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 622499EASTING MAP-NO
R/O FILE NO.
LOT 8600563NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65670716GIS LAT142.12803682GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TC 15AORIGINAL BORE NO
-BORE LINE
21/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYAUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
21/10/2014
21/10/2014
21/10/2014
21/10/2014
21/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
3.000
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
8.00
6.00
5.00
0.00
TOP(m)
11.00
11.00
11.00
6.00
5.00
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
1.20
4.50
7.00
STRATATOP (m)
1.20
4.50
7.00
8.00
STRATABOT (m)
SAND, SILTY, RED - SOME BAUXITE
CLAYS, SANDY, RED & IRONSTONE
SAND, CLAYEY, WHITE/YELLOW
SAND, WHITE, DRY, COARSE
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020618
2500-COOK
157576REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
5
6
RECORDNUMBER
8.00
9.00
STRATATOP (m)
9.00
11.50
STRATABOT (m)
KAOLIN, WHITE - DRY WITH SOME SAND
SAND, WHITE, COARSE *
STRATA DESCRIPTION
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
157576REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
SPECIAL WATER ANALYSIS
157576REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 11:00:59 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
BASIN 12-39-18LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-07-36LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 622336EASTING MAP-NO
R/O FILE NO.
LOT 8600767NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65486911GIS LAT142.12652794GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TC 2BORIGINAL BORE NO
-BORE LINE
21/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYAUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
31/10/2014
31/10/2014
31/10/2014
31/10/2014
31/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
3.000
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
1.00
0.50
0.25
0.00
TOP(m)
4.00
4.00
4.00
0.50
0.25
BOTTOM(m)
1
2
3
RECORDNUMBER
0.00
1.00
3.00
STRATATOP (m)
1.00
3.00
4.00
STRATABOT (m)
SAND, SILTY, RED
SAND, SILTY, RED, SOME BAUXITE
CLAYS, RED & GRAVELS, IRONSTONE
STRATA DESCRIPTION
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020617
2500-COOK
157569REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
157569REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 11:00:41 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-17LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-07-35LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 622336EASTING MAP-NO
R/O FILE NO.
LOT 8600776NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65478774GIS LAT142.12652758GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TC 2SAORIGINAL BORE NO
-BORE LINE
21/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
21/10/2014
21/10/2014
21/10/2014
21/10/2014
21/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
8.00
5.00
4.00
0.00
TOP(m)
12.50
12.50
12.50
5.00
4.00
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
1.00
3.00
5.00
STRATATOP (m)
1.00
3.00
5.00
7.00
STRATABOT (m)
SAND, SILTY, RED
SAND, SILTY, RED, SOME BAUXITE
CLAY, RED; GRAVELS, IRONSTONE
SAND, DRY, WHITE/YELLOW
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020616
2500-COOK
157568REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
5
RECORDNUMBER
7.00
STRATATOP (m)
12.50
STRATABOT (m)
CLAY, KAOLIN, HIT - CLAY, HARD *
STRATA DESCRIPTION
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
157568REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
SPECIAL WATER ANALYSIS
157568REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 11:00:13 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-10LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-07-26LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 622053EASTING MAP-NO
R/O FILE NO.
LOT 8600992NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65284585GIS LAT142.12391339GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TC 3SAORIGINAL BORE NO
-BORE LINE
20/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
20/10/2014
20/10/2014
20/10/2014
20/10/2014
20/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
8.00
5.50
4.50
0.00
TOP(m)
11.00
11.00
11.00
5.50
4.50
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
1.50
5.20
6.50
STRATATOP (m)
1.50
5.20
6.50
7.00
STRATABOT (m)
SAND, SILTY, RED
CEMENTED LAYER @ 1.5 CONTINUING INTO BAUXITE, IRONSTONE & CLAYS, RED
SAND, CLAYEY, WHITE/YELLOW
CLAY, SANDY, DRY, WHITE
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020614
2500-COOK
157566REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A
PIPE
07/10/2014
DATE
-4.80
MEASURE(m)
N
N/R RMK
5
RECORDNUMBER
7.00
STRATATOP (m)
11.00
STRATABOT (m)
SAND, COARSE, WHITE, SOME GRAVELS *
STRATA DESCRIPTION
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
157566REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
NR
MEASTYPE
MEASTYPE
MEASTYPE
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
SPECIAL WATER ANALYSIS
157566REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:59:46 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-22LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-54LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 621089EASTING MAP-NO
R/O FILE NO.
LOT 8600626NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65619224GIS LAT142.11505204GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TB2 SAORIGINAL BORE NO
-BORE LINE
20/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
20/10/2014
20/10/2014
20/10/2014
20/10/2014
20/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
10.50
7.00
6.00
0.00
TOP(m)
13.50
13.50
13.50
7.00
6.00
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
0.85
1.50
3.00
STRATATOP (m)
0.85
1.50
3.00
5.50
STRATABOT (m)
SAND, SILTY, RED
SAND, SILTY, RED SOME GRAVELS, IRONSTONE
CLAYS, RED & BAUXITE
CLAY, RED; GRAVELS, IRONSTONE
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020613
2500-COOK
157565REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
5
6
RECORDNUMBER
5.50
7.50
STRATATOP (m)
7.50
13.50
STRATABOT (m)
CLAY, SANDY, WHITE
SAND, COARSE/FINE, WHITE *
STRATA DESCRIPTION
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
157565REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
SPECIAL WATER ANALYSIS
157565REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:57:57 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-33LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-53LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 621057EASTING MAP-NO
R/O FILE NO.
LOT 8600291NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65922229GIS LAT142.11477056GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TB 1SAORIGINAL BORE NO
-BORE LINE
18/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
18/10/2014
18/10/2014
18/10/2014
18/10/2014
18/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
8.00
5.50
4.50
0.00
TOP(m)
11.00
11.00
11.00
5.50
4.50
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
0.70
5.00
7.00
STRATATOP (m)
0.70
5.00
7.00
11.00
STRATABOT (m)
SAND, SILTY, RED
CLAYS, RED WITH GRAVELS, IRONSTONE - SOME BAUXITE
SAND, DRY, COARSE, WHITE/YELLOW
SAND, FINE/COARSE, WHITE *
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020612
2500-COOK
157564REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
5
RECORDNUMBER
12.80
STRATATOP (m)
13.00
STRATABOT (m)
CLAY, KAOLIN
STRATA DESCRIPTION
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
157564REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
SPECIAL WATER ANALYSIS
157564REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:58:56 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
BASIN 12-39-33LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-53LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 621052EASTING MAP-NO
R/O FILE NO.
LOT 8600293NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.6592044GIS LAT142.11472444GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TB 1BORIGINAL BORE NO
-BORE LINE
18/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYAUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
18/10/2014
18/10/2014
18/10/2014
18/10/2014
18/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
2.50
1.00
0.50
0.00
TOP(m)
5.50
5.50
5.50
1.00
0.50
BOTTOM(m)
1
2
3
RECORDNUMBER
0.00
0.70
0.70
STRATATOP (m)
0.70
5.00
5.50
STRATABOT (m)
SAND, SILTY, RED
CLAYS, RED WITH GRAVELS, IRONSTONE AND BAUXITE
SAND, DRY COARSE, WHITE/YELLOW
STRATA DESCRIPTION
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020611
2500-COOK
157563REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
157563REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:58:33 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
BASIN 12-39-10LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-55LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 621130EASTING MAP-NO
R/O FILE NO.
LOT 8601013NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65269171GIS LAT142.11541434GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TB 3BORIGINAL BORE NO
-BORE LINE
18/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYAUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
18/10/2014
18/10/2014
18/10/2014
18/10/2014
18/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
1.50
1.00
0.50
0.00
TOP(m)
4.50
4.50
4.50
1.00
0.50
BOTTOM(m)
1
2
RECORDNUMBER
0.00
4.00
STRATATOP (m)
4.00
4.50
STRATABOT (m)
SAND, SILTY, RED; GRAVELS, IRONSTONE - SOME BAUXITE
CLAY, WHITE SANDY
STRATA DESCRIPTION
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9241
7024
MP41159
DRILL LOG # 1020610
2500-COOK
157562REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
157562REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:57:31 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-09LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-55LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 621125EASTING MAP-NO
R/O FILE NO.
LOT 8601026NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65257436GIS LAT142.1153678GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TB 3 SAORIGINAL BORE NO
-BORE LINE
18/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD, AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSMMROLES
A
A
A
A
A
PIPE
18/10/2014
18/10/2014
18/10/2014
18/10/2014
18/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
9.80
6.00
5.00
0.00
TOP(m)
12.80
12.80
12.80
6.00
5.00
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
4.00
6.00
10.00
STRATATOP (m)
4.00
6.00
10.00
12.80
STRATABOT (m)
SAND, SILTY, RED; IRONSTONE GRAVELS SOME BAUXITE
CLAY, SANDY, WHITE/YELLOW
SAND, FINE/COARSE; SOME LARGE STONES @ 9.5-10 *
SAND, COARSE, WHITE; CLAY TRACES
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9241
7024
MP41159
DRILL LOG # 1020609
2500-COOK
157561REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
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5
RECORDNUMBER
12.80
STRATATOP (m)
13.00
STRATABOT (m)
CLAY, KAOLIN, HIT WHITE
STRATA DESCRIPTION
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
157561REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
SPECIAL WATER ANALYSIS
157561REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:57:10 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-47LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-32LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 620402EASTING MAP-NO
R/O FILE NO.
LOT 8599869NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.66306288GIS LAT142.10875618GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TA 1SAORIGINAL BORE NO
-BORE LINE
17/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
17/10/2014
17/10/2014
17/10/2014
17/10/2014
17/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
9.50
8.00
7.00
0.00
TOP(m)
14.00
14.00
14.00
8.00
7.00
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
0.80
1.90
2.50
STRATATOP (m)
0.80
1.90
2.50
6.00
STRATABOT (m)
SAND, SILTY, RED
SILT, SANDY, RED; BAUXITE; CLAY, SILTY
IRONSTONE, CEMENTED
IRONSTONE GRAVELS; CLAY, RED WITH BAUXITE
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020608
2500-COOK
157560REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
5
6
7
RECORDNUMBER
6.00
8.00
13.90
STRATATOP (m)
8.00
13.90
14.00
STRATABOT (m)
SAND, COARSE, DRY, WHITE/YELLOW
SAND, FINE/COARSE, WHITE; TRACES OF CLAY *
CLAY, KAOLIN
STRATA DESCRIPTION
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
157560REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
SPECIAL WATER ANALYSIS
157560REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:56:43 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
BASIN 12-39-36LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-32LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 620430EASTING MAP-NO
R/O FILE NO.
LOT 8600200NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.66006915GIS LAT142.10900106GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TA 2BORIGINAL BORE NO
-BORE LINE
17/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYAUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
17/10/2014
17/10/2014
17/10/2014
17/10/2014
17/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
1.80
1.00
0.50
0.00
TOP(m)
4.80
4.80
4.80
1.00
0.50
BOTTOM(m)
1
2
RECORDNUMBER
0.00
1.00
STRATATOP (m)
1.00
4.80
STRATABOT (m)
SAND, SILTY RED
IRONSTONE GRAVELS; CLAYS, RED; SOME BAUXITE
STRATA DESCRIPTION
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020607
2500-COOK
157559REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
157559REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:56:23 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
BASIN 12-39-36LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-33LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 620434EASTING MAP-NO
R/O FILE NO.
LOT 8600205NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.6600238GIS LAT142.10903769GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TA2 5AORIGINAL BORE NO
-BORE LINE
16/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
16/10/2014
16/10/2014
16/10/2014
16/10/2014
16/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
9.20
6.00
5.00
0.00
TOP(m)
13.70
13.70
13.70
6.00
5.00
BOTTOM(m)
1
2
3
RECORDNUMBER
0.00
1.00
5.50
STRATATOP (m)
1.00
5.50
13.70
STRATABOT (m)
SAND, SILTY, RED
IRONSTONE GRAVELS; CLAYS, RED
SAND, FINE/COARSE, WHITE - 50ML TRACER OF CLAY *
STRATA DESCRIPTION
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020606
2500-COOK
157558REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
157558REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:56:01 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
BASIN 12-39-23LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-34LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 620474EASTING MAP-NO
R/O FILE NO.
LOT 8600602NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65643289GIS LAT142.10939048GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TA3BORIGINAL BORE NO
-BORE LINE
16/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYAUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
16/10/2014
16/10/2014
16/10/2014
16/10/2014
16/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
2.00
1.00
0.50
0.00
TOP(m)
5.00
5.00
5.00
1.00
0.50
BOTTOM(m)
1
2
3
RECORDNUMBER
0.00
2.00
4.00
STRATATOP (m)
2.00
4.00
5.00
STRATABOT (m)
SAND, SILTY RED
CLAYS, RED; IRONSTONE GRAVELS WITH SOME BAUXITE
SANDS, YELLOW/BROWNISH; SOME CLAYS
STRATA DESCRIPTION
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020605
2500-COOK
157557REG NUMBER
DATA OWNER
28-OCT-14DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 3
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
157557REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
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1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:55:35 AM **
1Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-23LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-06-34LONGITUDE MAP-SERIES
RN DRAWERD/O FILE NO.
SHIRE 620465EASTING MAP-NO
R/O FILE NO.
LOT 8600602NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION GPSACCURACY
30GPS ACC
PRES EQUIPMENT
YCHECKED
-12.65643323GIS LAT142.10930761GIS LNG
4957-WEIPAPARISH NAME
COUNTY
TA3 SAORIGINAL BORE NO
-BORE LINE
16/10/2014DATE DRILLED
POLYGON
KELLY, KIRKDRILLERS NAME
RN OF BORE REPLACED
SAXON DRILLINGDRILL COMPANYROTARY MUD AUGERMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUSSMROLES
A
A
A
A
A
PIPE
16/10/2014
16/10/2014
16/10/2014
16/10/2014
16/10/2014
DATE
1
2
3
4
5
RECORDNUMBER
Polyvinyl Chloride
Perforated or Slotted Casing
Gravel Pack
Bentonite Seal
Grout
MATERIAL DESCRIPTION
5.000
0.400
2.500
MAT SIZE(mm)
WT
AP
GR
SIZE DESC
60
60
125
125
125
OUTSIDEDIAM(mm)
0.00
8.00
6.00
5.00
0.00
TOP(m)
14.00
12.50
14.00
6.00
5.00
BOTTOM(m)
1
2
3
4
RECORDNUMBER
0.00
1.50
5.20
7.00
STRATATOP (m)
1.50
5.20
7.00
9.00
STRATABOT (m)
SAND, SILTY RED
CLAYS, RED; IRONSTONE/GRAVELS
SANDS, WHITE/YELLOW; SOME CLAYS
CLAY, SANDY, WHITE *
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
Mareeba
REGISTRATION DETAILS
9240
7024
MP41159
DRILL LOG # 1020604
2500-COOK
157556REG NUMBER
DATA OWNER
28-FEB-15DATE LOG RECD
2Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
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5
6
7
RECORDNUMBER
9.00
12.00
13.70
STRATATOP (m)
12.00
13.70
14.00
STRATABOT (m)
SAND, COARSE, WHITE; VERY LITTLE CLAY, SOME STONES 1" DIA.
BECOMING, YELLOW/WHITE
CLAY, KAOLIN; SOME COARSE SAND
STRATA DESCRIPTION
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
157556REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
3Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
SPECIAL WATER ANALYSIS
157556REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page06/03/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 06/03/2017 10:55:01 AM **
1Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-38-54LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-03-03LONGITUDE MAP-SERIES
D/O FILE NO.
SHIRE 614120EASTING SD5403MAP-NO
R/O FILE NO.
LOT 8601526NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
PRES EQUIPMENT
YCHECKED
-12.648316872GIS LAT142.050849903GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
COMALCO NO.20ORIGINAL BORE NO
-BORE LINE
09/08/1970DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
1
2
3
4
5
6
7
8
9
10
11
RECORDNUMBER
0.00
0.46
3.66
4.11
STRATATOP (m)
0.46
3.66
4.11
6.32
STRATABOT (m)
SILTY CLAY: FIRM, DRY, DARK GREY;
OF MEDIUM PLASTICITY
BAUXITE GRAVEL: MEDIUM DENSE, POORLY
GRADED, MEDIUM TO FINE GRAINED,
ROUNDED; WITH A TRACE OF ORANGE-BROWN
SILTY CLAY
IRONSTONE AND GRAVELLY SAND: MEDIUM
DENSE; WITH SOME BAUXITE GRAVEL
AND A TRACE OF ORANGE-BROWN,
SILTY CLAY
SILTY CLAY: VERY FIRM TO STIFF,
STRATA DESCRIPTION
STRATA LOG DETAILS
CASING DETAILS
M
254
Mareeba
REGISTRATION DETAILS
9241
7024
MPH41159
2500-COOK
92282REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
DNR
DNR
SOURCE
1
2
RECORDNUMBER
0.00
4.10
STRATATOP (m)
4.10
12.50
STRATABOT (m)
BULIMBA FORMATION
BULIMBA FORMATION
STRATA DESCRIPTION
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
RECORDNUMBER
6.32
6.78
11.89
STRATATOP (m)
6.78
11.89
12.50
12.50
STRATABOT (m)
MOIST, WHITE, MOTTLED WITH YELLOW-
BROWN; OF MEDIUM TO HIGH PLASTICITY;
WITH CONSIDERABLE MEDIUM TO FINE
GRAINED, ANGULAR, QUARTZOSE SAND
SAND: MEDIUM DENSE, WELL GRADED,
ANGULAR, QUARTZOSE; WITH A TRACE OF
KAOLINITIC SILTY CLAY AND A TRACE OF
IRONSTONE GRAVEL
SAND: MEDIUM DENSE, POORLY GRADED,
MEDIUM TO FINE GRAINED, ANGULAR,
QUARTZOSE; WITH A TRACE OF WHITE,
SILTY CLAY
SILTY CLAY: STIFF, MOIST, WHITE,
KAOLINITIC; OF MEDIUM TO HIGH
PLASTICITY
************ TOTAL DEPTH ************
REFER TO: COFFEY & HOLLINGSWORTH,
1971 - SHALLOW AQUIFER INVESTIGATION
WEIPA, NOTH QLD. REP. TO COAMLCO
LTD (UNPUBL.)
STRATA DESCRIPTION
AQUIFER DETAILS
STRATIGRAPHY DETAILS
PUMP TEST DETAILS PART 1
92282REG NUMBER
**** NO RECORDS FOUND ****
3Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
PUMP TEST DETAILS PART 2
BORE CONDITION
SPECIAL WATER ANALYSIS
92282REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 20/06/2017 03:48:48 PM **
1Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-58LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-02-54LONGITUDE MAP-SERIES
463D/O FILE NO.
SHIRE 613837EASTING MD6601-A1MAP-NO
R/O FILE NO.
LOT 8599583NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
NEPRES EQUIPMENT
YCHECKED
-12.66589175GIS LAT142.04831813GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
SA 63ORIGINAL BORE NO
-BORE LINE
DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
A
PIPE
01/01/1976
DATE
1
RECORDNUMBER
Screen
MATERIAL DESCRIPTION MAT SIZE(mm)
SIZE DESC OUTSIDEDIAM(mm)
TOP(m)
13.50
BOTTOM(m)
1
2
3
4
RECORDNUMBER
STRATATOP (m)
STRATABOT (m)
STRATA DETAILS UNKNOWN
SCREEN SEATED - 13.52M
NO OTHER DETAILS AVAILABLE
DRILLED BY COMALCO
STRATA DESCRIPTION
AQUIFER DETAILS
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
M
503
Mareeba
REGISTRATION DETAILS
9241
7024
MP41159
COMALCO
2500-COOK
99254REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A AA A AA A AA
PIPE
29/01/1976 31/03/1976 21/04/197623/06/1976 23/07/1976 24/09/197628/10/1976 30/11/1976 24/12/197625/02/1977
DATE
-5.49 -3.51 -4.34-6.96 -7.57 -8.59-9.01 -9.42 -9.49-5.50
MEASURE(m)
R R RR R RR R RR
N/R RMK
AX
PIPE
29/01/197629/01/1976
DATE
33.7033.22
ELEVATION
ASDASD
DATUM
SVYSVY
PRECISION
RN
MEASUREMENT POINT
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
99254REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
SURVEY SOURCE
NR NR NRNR NR NRNR NR NRNR
MEASTYPE
MEASTYPE
MEASTYPE
3Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
SPECIAL WATER ANALYSIS
99254REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 20/06/2017 03:55:13 PM **
1Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
BASIN 12-39-01LATITUDE MAP-SCALE
OFFICE SUB-AREA 142-02-56LONGITUDE MAP-SERIES
463D/O FILE NO.
SHIRE 613894EASTING MD6601-A1MAP-NO
R/O FILE NO.
LOT 8601308NORTHING MAP NAME
H/O FILE NO.
PLAN 54ZONE PROG SECTIONORIGINAL DESCRIPTION SKETACCURACY
GPS ACC
NEPRES EQUIPMENT
YCHECKED
-12.650292285GIS LAT142.048781596GIS LNG
1873-FIFEPARISH NAME
WEIPACOUNTY
SA 69ORIGINAL BORE NO
-BORE LINE
DATE DRILLED
POLYGON
DRILLERS NAME
RN OF BORE REPLACED
DRILL COMPANYMETHOD OF CONST.
Sub-Artesian FacilityFACILITY TYPE
ExistingSTATUS
ROLES
A
PIPE
01/01/1976
DATE
1
RECORDNUMBER
Screen
MATERIAL DESCRIPTION MAT SIZE(mm)
SIZE DESC OUTSIDEDIAM(mm)
TOP(m)
11.90
BOTTOM(m)
1
2
3
4
RECORDNUMBER
STRATATOP (m)
STRATABOT (m)
STRATA DETAILS UNKNOWN
SCREEN SEATED - 11.94M
NO OTHER DETAILS AVAILABLE
DRILLED BY COMALCO
STRATA DESCRIPTION
AQUIFER DETAILS
STRATIGRAPHY DETAILS
STRATA LOG DETAILS
CASING DETAILS
M
503
Mareeba
REGISTRATION DETAILS
9241
7024
MP41159
COMALCO
2500-COOK
99253REG NUMBER
**** NO RECORDS FOUND ****
DATA OWNER
DATE LOG RECD
2Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
A A AA A AA A AA
PIPE
29/01/1976 31/03/1976 21/04/197623/06/1976 23/07/1976 24/09/197628/10/1976 30/11/1976 24/12/197625/02/1977
DATE
-7.20 -3.54 -4.05-7.00 -7.81 -9.02-9.49 -9.89 -9.94-6.34
MEASURE(m)
R R RR R RR R RR
N/R RMK
AX
PIPE
29/01/197629/01/1976
DATE
34.6034.16
ELEVATION
ASDASD
DATUM
SVYSVY
PRECISION
RN
MEASUREMENT POINT
FIELD MEASUREMENTS
WIRE LINE LOG DETAILS
WATER LEVEL DETAILS
WATER ANALYSIS PART 2
WATER ANALYSIS PART1
ELEVATION DETAILS
PUMP TEST DETAILS PART 1
PUMP TEST DETAILS PART 2
BORE CONDITION
PIPE DATE MEASURE(m)
N/R RMK PIPE DATE MEASURE(m)
N/R RMK
99253REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
SURVEY SOURCE
NR NR NRNR NR NRNR NR NRNR
MEASTYPE
MEASTYPE
MEASTYPE
3Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
SPECIAL WATER ANALYSIS
99253REG NUMBER
**** NO RECORDS FOUND ****
**** NO RECORDS FOUND ****
4Page20/06/2017DATE GROUNDWATER DATABASE
BORE REPORT
of 4
1
2
3
Open Licence (Single Supply)
Permitted use: - You may use the supplied data for your own purposes (including supply to consultants for a specific consultancy project for you but the consultants must return or destroy the supplied data when the project is finished). You must not sell or distribute the supplied data. - You must display this copyright notice on any copies of the supplied data however altered, reformatted or redisplayed if you supply to a consultant or copy for back up purposes: “© State of Queensland 2017”. - You may create and distribute hardcopy and digital products based on or containing the supplied data, provided all the following conditions are met: - You must display this acknowledgment on the product(s): “Based on or contains data provided by the State of Queensland 2017. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws.” - You must include metadata with the product(s) you create that use or incorporate the supplied data and the metadata must incorporate as a minimum the metadata provided with this supplied data.
Obligations:
- You must not use the data for direct marketing or in breach of the privacy laws.
Ownership:
The State of Queensland is the owner of the intellectual property rights in and to the supplied data or has the right to make this supplied data available.
Disclaimer and indemnity:You agree to accept all responsibility and risks associated with the use of the supplied data. The State makes no representations or warranties in relation to the supplied data, and, you agree that, to the extent permitted by law, all warranties relating to accuracy, reliability, completeness, currency or suitability for any particular purpose and all liability for any loss, damage or costs (including consequential damage) incurred in any way (including but not limited to that arising from negligence) in connection with any use of or reliance on the supplied data are excluded or limited. You agree to continually indemnify the State ofQueensland (and its officers and employees) against any loss, cost, expense, damage and liability of any kind (including consequential damage and liability innegligence) arising directly or indirectly from or related to any claim relating to your use of the supplied data or any product made from the data.
** End of Report. Produced: 20/06/2017 03:53:42 PM **
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX F Borehole logs
L
M
L
FILL: Silty SANDdark brown, fine sand, some rootlets
FILL: Clayey SANDred brown, fine to medium grained sand, fine to mediumsubrounded to angular gravels of quartz and bauxite
Clayey Gravelly SANDred brown, fine to medium grained sand, fine rounded to angulargravels of bauxite, trace of silt
fine to medium rounded to angular gravels of bauxite andironstone
Clayey SANDred brown, no gravels, fine to medium sand, trace of silt
Clayey Gravelly SANDred brown, fine to medium rounded to subrounded gravels ofbauxite, fine to medium grained sand, trace of silt
Clayey SANDred brown, fine to medium sand, trace gravels, borderline sandyclay, trace of silt
Silty SANDyellow brown with red, fine to coarse sand, minor clay
white colour, some fine subangular to angular quartz gravels
fine to medium angular to subrounded quartz gravels, increasedgravel size downhole, white/very pale brown colour
Clayey SANDpale brown, red mottled, fine to coarse grained sand, fine tomedium subrounded to subangular gravels of quartz
Sandy CLAYmedium plasticity, pale brown, fine to medium grained sand, fineto medium subangular to angular gravels, minor red mottling
fine sand, rounded to subrounded gravels of quartz (fine tomedium), som white kaolin clasts that are moist and soft to firm
CLAYmedium plasticity, pale brown, trace of fine sand, trace of gravels,some moist soft to firm white clay clasts of kaolin
mottled red and yellow, no gravels
red clay, minor white clay clasts/mottling, some mud on the augerstem, water bearing zone, drilling resistance lessened
white clay clasts, pale brown clay
white clay
CLAYmedium plasticity, pale brown, some fine to medium sand
Sandy CLAYmedium plasticity, fine to coarse sand (salt and pepper coloured),brown colour
END OF BOREHOLE @ 22.50 m
SMSCSC
SC
SC
SC
SC
SC
CL
CH
CH
CL
0.50
1.20
2.00
6.00
7.50
8.00
9.50
11.00
12.00
13.00
15.00
16.75
17.30
18.50
19.00
20.00
21.00
43.9643.76
43.26
42.46
38.46
36.96
36.46
34.96
33.46
32.46
31.46
29.46
27.71
27.16
25.96
25.46
24.46
23.46
21.96
HA
AD
V
1218 - BH022 0.70-0.75 m170512
1218 - BH022 7.50-7.75 m170513
1218 - BH022 11.50-11.75 m170513
1218 - BH022 16.75-17.00 m170513
1218 - BH022 22.00-22.25 m170515
DD - M
M
M -W
M
D - M
M
M -W
W
L
MD
L
St
F
F - St
VS -S
S - F
GatticTop cap
Grout
Casing PVCclass 18 50mmID
Bentonite pellets
Filter pack sand2.5 - 3.0mm
Factory slottedscreen 0.4mm
End cap
Sump
SHEET: 1 OF 1
Field Material DescriptionSamplingDrilling
PE
NE
TR
AT
ION
RE
SIS
TA
NC
E
SOIL/ROCK MATERIAL DESCRIPTION
US
CS
SY
MB
OL
RE
CO
VE
RE
D
WA
TE
R
RLDEPTH
DE
PT
H(m
etre
s)
ME
TH
OD
GR
AP
HIC
LOG
SAMPLE ORFIELD TEST
GAP gINT FN. F01dRL3
CLIENT:
PROJECT:
LOCATION:
JOB NO:
DATE: 12/5/17
DATE: 12/6/17
This report of borehole must be read in conjunction with accompanying notes and abbreviations. It has been prepared forgeotechnical purposes only, without attempt to assess possible contamination. Any references to potential contamination are for
information only and do not necessarily indicate the presence or absence of soil or groundwater contamination.
REPORT OF BOREHOLE: BH022
Defence
Scherger PSI
Weipa
1669283
COORDS: 617529.3 m E 8604009.5 m N MGA94 56
SURFACE RL: 44.46 m DATUM: AHD
INCLINATION: -90°
HOLE DIA: 125 mm HOLE DEPTH: 22.50 m
DRILL RIG:
CONTRACTOR: Saxon Drilling
LOGGED: BJV
CHECKED: ELC
GA
P 8
_15.
0 LI
B.G
LB L
og G
AP
NO
N-C
OR
ED
FU
LL P
AG
E 1
6692
83.
GP
J <
<D
raw
ingF
ile>
> 2
7/07
/201
7 13
:50
8.3
0.00
4 D
atge
l Too
ls
MO
IST
UR
EC
ON
DIT
ION
CO
NS
IST
EN
CY
DE
NS
ITY PIEZOMETER DETAILS
0
5
10
15
20
L
M
L
Sandy CLAYmedium plasticity, red brown, borderline clayey sand, fine tomedium sand
Clayey Gravelly SANDfine to medium sand, fine to medium rounded to subroundedgravels of bauxite, borderline sandy clay
Clayey Gravelly SANDred brown, fine to medium sand, fine to medium subrounded toangular gravels of ironstone, harder resistance drilling
increasing moisture downhole, fine to coarse sand, yellow brownmottled with red brown, trace fine to coarse subrounded tosubangular gravels of quartz
yellow brown, minor mottling, decreased gravel content
rounded to subrounded fine to medium gravels of quartz,increased clay content
Sandy CLAYmedium plasticity, pale brown, fine to medium sand
Sandy CLAYhigh plasticity, brown, fine to coarse grained sand
decreased sand content, fine grained sand
CLAYhigh plasticity, mottled white clay with red brown colour, traces offine grained sand, some minor yellow mottling
END OF BOREHOLE @ 21.50 m
CL
SC
CL
CH
0.90
1.50
4.50
6.00
7.00
9.00
11.60
12.00
13.50
44.50
43.60
43.00
40.00
38.50
37.50
35.50
32.90
32.50
31.00
23.00
HA
AD
V
1218 - BH023 0.60-0.75 m170509R = 0A
1218 - BH023 1.90-2.00 m170509R = 0A
1218 - BH023 4.50-4.75 m170510R = 0A
1218 - BH023 13.80-14.00 m170510R = 0A
1218 - BH023 16.80-17.00 m170510R = 0A
M
D - M
M
W
S
L
MD
L
St
F
St
F - St
S
GatticTop cap
Grout
Casing class 1850mm ID
Bentonite pellets
Sand 2.5 - 3.0mm
Factory slottedscreen 0.4mm
End capSump
SHEET: 1 OF 1
Field Material DescriptionSamplingDrilling
PE
NE
TR
AT
ION
RE
SIS
TA
NC
E
SOIL/ROCK MATERIAL DESCRIPTION
US
CS
SY
MB
OL
RE
CO
VE
RE
D
WA
TE
R
RLDEPTH
DE
PT
H(m
etre
s)
ME
TH
OD
GR
AP
HIC
LOG
SAMPLE ORFIELD TEST
GAP gINT FN. F01dRL3
CLIENT:
PROJECT:
LOCATION:
JOB NO:
DATE: 10/5/17
DATE: 12/6/17
This report of borehole must be read in conjunction with accompanying notes and abbreviations. It has been prepared forgeotechnical purposes only, without attempt to assess possible contamination. Any references to potential contamination are for
information only and do not necessarily indicate the presence or absence of soil or groundwater contamination.
REPORT OF BOREHOLE: BH023
Defence
Scherger PSI
Weipa
1669283
COORDS: 617970.6 m E 8603882.9 m N MGA94 56
SURFACE RL: 44.50 m DATUM: AHD
INCLINATION: -90°
HOLE DIA: 125 mm HOLE DEPTH: 21.50 m
DRILL RIG:
CONTRACTOR: Saxon Drilling
LOGGED: BJV
CHECKED: ELC
GA
P 8
_15.
0 LI
B.G
LB L
og G
AP
NO
N-C
OR
ED
FU
LL P
AG
E 1
6692
83.
GP
J <
<D
raw
ingF
ile>
> 2
7/07
/201
7 13
:50
8.3
0.00
4 D
atge
l Too
ls
MO
IST
UR
EC
ON
DIT
ION
CO
NS
IST
EN
CY
DE
NS
ITY PIEZOMETER DETAILS
0
5
10
15
20
M
L
M
FILL: Silty SANDbrown, trace rootlets, fine to medium sand, angular to subangulargravels
FILL: Clayey Gravelly SANDred brown, fine to medium sand, fine to medium subrounded torounded gravels of bausite, borderline sandy clay
FILL: Clayey Sandy GRAVELfine to coarse angualr gravel of bluestone, fine and medium sand
FILL: Clayey Gravelly SANDred brown, fine to medium sand, fine to medium subrounded toangular gravels of bausite and bluestone, borderline sandy clay
FILL: Sandy CLAYmedium plasticity, red brown, fine and medium sand, no gravels
Clayey SANDred brown, fine to medium sand, fine to medium subrounded toangualr gravels of ironstone, borderline sandy clay
Clayey SANDyellow brown, fine to coarse sand, trace gravels of ironstone
increased clay content downhole
some white clay clast, some fine angular to subrounded gravelsof quartz
harder resistance drilling, increased stiff clay clasts of kaolin
Sandy CLAYmedium plasticity, brown to red brown, fine to medium sand,some white clay clasts
brown, trace gravels
CLAYhigh plasticity, brown, with some yellow mottling, some white clayclasts, trace sand
mud on augers
Sandy CLAYhigh plasticity, brown, fine to medium sand, trace fine to coarsesandstone fragments
END OF BOREHOLE @ 22.50 m
SMSCGCSCCL
SC
CL
CH
CL
0.33
1.00
2.00
5.00
6.00
7.00
10.50
11.00
12.20
14.50
17.00
18.00
20.00
43.44
42.96
41.96
38.96
37.96
36.96
33.46
32.96
31.76
29.46
26.96
25.96
23.96
21.46
HA
AD
V
1218 - BH024 0.80-1.00 m1705R = 0A
1218 - BH024 8.50-8.75 mR = 0A
1218 - BH024 12.50-12.75 m1705R = 0A
1218 - BH024 16.50-16.75 m1705R = 0A
1218 - BH024 21.50-21.75 m1705R = 0A
D
M
D - M
D
M
M -W
W
MD
MD -D
S
L -MD
L
St
F - St
S
F
GatticTop cap
Casing PVCcasing, 50mmID
Grout
Bentonite pellets
Factory slottedscreen 0.4mm
Sand 2.5 -3.0mm
End cap
Sump
SHEET: 1 OF 1
Field Material DescriptionSamplingDrilling
PE
NE
TR
AT
ION
RE
SIS
TA
NC
E
SOIL/ROCK MATERIAL DESCRIPTION
US
CS
SY
MB
OL
RE
CO
VE
RE
D
WA
TE
R
RLDEPTH
DE
PT
H(m
etre
s)
ME
TH
OD
GR
AP
HIC
LOG
SAMPLE ORFIELD TEST
GAP gINT FN. F01dRL3
CLIENT:
PROJECT:
LOCATION:
JOB NO:
DATE: 12/5/17
DATE: 12/6/17
This report of borehole must be read in conjunction with accompanying notes and abbreviations. It has been prepared forgeotechnical purposes only, without attempt to assess possible contamination. Any references to potential contamination are for
information only and do not necessarily indicate the presence or absence of soil or groundwater contamination.
REPORT OF BOREHOLE: BH024
Defence
Scherger PSI
Weipa
1669283
COORDS: 616647.2 m E 8604067.7 m N MGA94 56
SURFACE RL: 43.96 m DATUM: AHD
INCLINATION: -90°
HOLE DIA: 125 mm HOLE DEPTH: 22.50 m
DRILL RIG:
CONTRACTOR: Saxon Drilling
LOGGED: BJV
CHECKED: ELC
GA
P 8
_15.
0 LI
B.G
LB L
og G
AP
NO
N-C
OR
ED
FU
LL P
AG
E 1
6692
83.
GP
J <
<D
raw
ingF
ile>
> 2
7/07
/201
7 13
:50
8.3
0.00
4 D
atge
l Too
ls
MO
IST
UR
EC
ON
DIT
ION
CO
NS
IST
EN
CY
DE
NS
ITY PIEZOMETER DETAILS
0
5
10
15
20
L
M
L
Silty SANDred brown, trace rootlets, fine to medium grained sand
Clayey Gravelly SANDfine to medium grained sand, fine to medium subrounded torounded gravels of bauxite, borderline sandy clay
brown, with dark brown mottling, some gravels
Sandy Gravelly CLAYred brown, fine to medium grained sand, subrounded tosubangular fine to medium gravels of ironstone
increased clay content
Clayey SANDyellow brown, some mottling, fine to medium grained sand
SANDwhite, minor red brown mottling, fine to coarse sand, some finesubangular quartz gravels
increased moisture, no mottling
some white clay clasts
increasing clay clasts content downhole
Sandy CLAYpale brown, fine to medium grained sand, some white clay clasts
brown, decreasing sand content downhole
CLAYbrown, some white and yellow mottling, some fine sand, highplasticity
white, with some red and yellow mottling
END OF BOREHOLE @ 22.50 m
SM
SC
CL
SC
SW
CL
CH
0.45
1.00
3.50
4.50
5.30
7.00
10.00
10.40
11.00
13.50
15.00
16.80
21.00
43.47
42.92
40.42
39.42
38.62
36.92
33.92
33.52
32.92
30.42
28.92
27.12
22.92
21.42
HA
AD
V
1218-BH025 0.60-0.75 m170510R = 0A
1218-BH025 7.50-7.75 m170511R = 0A
1218-BH025 11.50-11.75 m170511R = 0A
1218-BH025 16.50-16.75 m170511R = 0A
1218-BH025 22.25-22.50 m170511
D - M
M
D
M
D
M
W
L
MD
L
S
L
St
S
GatticTop Cap
Grout
PVC casingclass 18 50mmID
Bentonite pellets
Filter pack sand2.5 - 3.0mm size
Factory slottedscreen 0.4mm
End capSump
SHEET: 1 OF 1
Field Material DescriptionSamplingDrilling
PE
NE
TR
AT
ION
RE
SIS
TA
NC
E
SOIL/ROCK MATERIAL DESCRIPTION
US
CS
SY
MB
OL
RE
CO
VE
RE
D
WA
TE
R
RLDEPTH
DE
PT
H(m
etre
s)
ME
TH
OD
GR
AP
HIC
LOG
SAMPLE ORFIELD TEST
GAP gINT FN. F01dRL3
CLIENT:
PROJECT:
LOCATION:
JOB NO:
DATE: 11/5/17
DATE: 12/6/17
This report of borehole must be read in conjunction with accompanying notes and abbreviations. It has been prepared forgeotechnical purposes only, without attempt to assess possible contamination. Any references to potential contamination are for
information only and do not necessarily indicate the presence or absence of soil or groundwater contamination.
REPORT OF BOREHOLE: BH025
Defence
Scherger PSI
Weipa
1669283
COORDS: 616943.9 m E 8604111.0 m N MGA94 56
SURFACE RL: 43.92 m DATUM: AHD
INCLINATION: -90°
HOLE DIA: 125 mm HOLE DEPTH: 22.50 m
DRILL RIG:
CONTRACTOR: Saxon Drilling
LOGGED: BJV
CHECKED: ELC
GA
P 8
_15.
0 LI
B.G
LB L
og G
AP
NO
N-C
OR
ED
FU
LL P
AG
E 1
6692
83.
GP
J <
<D
raw
ingF
ile>
> 2
7/07
/201
7 13
:50
8.3
0.00
4 D
atge
l Too
ls
MO
IST
UR
EC
ON
DIT
ION
CO
NS
IST
EN
CY
DE
NS
ITY PIEZOMETER DETAILS
0
5
10
15
20
R = 0A
SHEET: 2 OF 1
Field Material DescriptionSamplingDrilling
PE
NE
TR
AT
ION
RE
SIS
TA
NC
E
SOIL/ROCK MATERIAL DESCRIPTION
US
CS
SY
MB
OL
RE
CO
VE
RE
D
WA
TE
R
RLDEPTH
DE
PT
H(m
etre
s)
ME
TH
OD
GR
AP
HIC
LOG
SAMPLE ORFIELD TEST
GAP gINT FN. F01dRL3
CLIENT:
PROJECT:
LOCATION:
JOB NO:
DATE: 11/5/17
DATE: 12/6/17
This report of borehole must be read in conjunction with accompanying notes and abbreviations. It has been prepared forgeotechnical purposes only, without attempt to assess possible contamination. Any references to potential contamination are for
information only and do not necessarily indicate the presence or absence of soil or groundwater contamination.
REPORT OF BOREHOLE: BH025
Defence
Scherger PSI
Weipa
1669283
COORDS: 616943.9 m E 8604111.0 m N MGA94 56
SURFACE RL: 43.92 m DATUM: AHD
INCLINATION: -90°
HOLE DIA: 125 mm HOLE DEPTH: 22.50 m
DRILL RIG:
CONTRACTOR: Saxon Drilling
LOGGED: BJV
CHECKED: ELC
GA
P 8
_15.
0 LI
B.G
LB L
og G
AP
NO
N-C
OR
ED
FU
LL P
AG
E 1
6692
83.
GP
J <
<D
raw
ingF
ile>
> 2
7/07
/201
7 13
:50
8.3
0.00
4 D
atge
l Too
ls
MO
IST
UR
EC
ON
DIT
ION
CO
NS
IST
EN
CY
DE
NS
ITY PIEZOMETER DETAILS
25
30
35
40
45
L
M
L
Gravelly Silty SANDbrown, fine to medium gravels, subrounded to angular, fine tomedium sand
Sandy CLAYmedium plasticity, red brown, borderline clayey sand, fine tomedium sand grains, no gravels
Sandy GRAVELred brown, fine to medium rounded to subrounded gravels ofbauxite, fine to medium grained sand, some clay
harder resistance drilling, starting to come into ironstone layer
Clayey SANDred brown, fine to medium grained sand, some fine to mediumsubrounded to angular gravels of ironstone and minor bauxite,trace coarse gravels
Silty SANDyellow, yellow is brownish, fine to coarse, minor clay, somesubrounded gravels
white colouring, increasing moisture downhole
increased clay content downhole
Clayey SANDwhite, fine to medium sand
Clayey SANDhigh plasticity, white, fine grained sand
END OF BOREHOLE @ 14.00 m
SC
CL
GC
SC
SM
SC
0.40
0.90
3.00
5.50
6.00
7.00
7.50
13.40
38.93
38.43
36.23
33.83
33.33
32.33
31.83
25.93
25.33
HA
AD
V
1218 - BH026 0.60-0.75 m170509R = 0A1218 - BH026 1.40-1.50 m170509R = 0A
1218 - BH026 7.00-7.25 m170509R = 0A
1218 - BH026 13.40-13.55 m170509R = 0A
D - M
M
W
MD
S
L
L -MD
L
F - St
GatticTop cap
50mm ID PVCclass 18 casing
Bentonite pellets
Factory slottedscreen 0.4mm
Filter pack sand2.5 - 3.0 m
End cap
SHEET: 1 OF 1
Field Material DescriptionSamplingDrilling
PE
NE
TR
AT
ION
RE
SIS
TA
NC
E
SOIL/ROCK MATERIAL DESCRIPTION
US
CS
SY
MB
OL
RE
CO
VE
RE
D
WA
TE
R
RLDEPTH
DE
PT
H(m
etre
s)
ME
TH
OD
GR
AP
HIC
LOG
SAMPLE ORFIELD TEST
GAP gINT FN. F01dRL3
CLIENT:
PROJECT:
LOCATION:
JOB NO:
DATE: 9/5/17
DATE: 12/6/17
This report of borehole must be read in conjunction with accompanying notes and abbreviations. It has been prepared forgeotechnical purposes only, without attempt to assess possible contamination. Any references to potential contamination are for
information only and do not necessarily indicate the presence or absence of soil or groundwater contamination.
REPORT OF BOREHOLE: BH026
Defence
Scherger PSI
Weipa
1669283
COORDS: 616721.2 m E 8601407.5 m N MGA94 56
SURFACE RL: 39.33 m DATUM: AHD
INCLINATION: -90°
HOLE DIA: 125 mm HOLE DEPTH: 14.00 m
DRILL RIG:
CONTRACTOR: Saxon Drilling
LOGGED: BJV
CHECKED: ELC
GA
P 8
_15.
0 LI
B.G
LB L
og G
AP
NO
N-C
OR
ED
FU
LL P
AG
E 1
6692
83.
GP
J <
<D
raw
ingF
ile>
> 2
7/07
/201
7 13
:50
8.3
0.00
4 D
atge
l Too
ls
MO
IST
UR
EC
ON
DIT
ION
CO
NS
IST
EN
CY
DE
NS
ITY PIEZOMETER DETAILS
0
5
10
15
20
L
M
L
Silty SANDbrown, fine grained sand with minor medium grained sand
brownish orange, fine to medium sand, some fine subrounded tosubangular gravels, minor clay
Silty Sandy GRAVELred brown, fine to cobble sized subangular to subrounded gravelsof ironstone, fine to medium sand
Silty Sandy CLAYlow - medium plasticity, orange brown, fine to medium grainedsand, minor fine subrounded gravels of bauxite
harder band of gravels drilled through
Silty Sandy CLAYorange brown, fine to medium grained sand, minor finesubrounded gravels of bauxite and ironstone
Silty Sandy CLAYmedium plasticity, yellow red, mottled colouring, coming into whitekaolin, some white clay clasts, trace of gravels
increasing clay content downhole
Silty CLAYmedium plasticity, pale brown, mottled with white kaolin clasts,trace of fine subrounded to subangular gravels
increasing white kaolin content downhole
Silty CLAYhigh plasticity, white kaolin, pale pink / brown colour due to mixingwith above soil profile as it comes up the auger
brown, some white clasts
Silty Sandy CLAYmedium plasticity, brown, fine to medium sand, minor finesubangular gravels
END OF BOREHOLE @ 13.50 mSWL @ 7.5 mbgl
SM
GM
CL
CL
CH
CL
0.40
1.00
2.80
4.70
6.00
6.80
8.00
10.50
11.50
12.00
21.90
21.30
19.5019.30
17.60
16.30
15.50
14.30
11.80
10.80
10.30
8.80
HA
AD
V
1218-BH021 0.50-0.75 m170508R = 0A1218-BH021 0.90-1.00 m170508R = 0A
1218-BH021 7.80-8.00 m170508R = 0A
D
M
M -W
W
L - DD -VD
MD
D
S - F
S
Monument
Top cap
PVC casing50mm ID
Grout
Bentonite pellets
Filter pack sand2.5 - 3.0mm size
Factory slottedscreen 0.4mm
End cap
SHEET: 1 OF 1
Field Material DescriptionSamplingDrilling
PE
NE
TR
AT
ION
RE
SIS
TA
NC
E
SOIL/ROCK MATERIAL DESCRIPTION
US
CS
SY
MB
OL
RE
CO
VE
RE
D
WA
TE
R
RLDEPTH
DE
PT
H(m
etre
s)
ME
TH
OD
GR
AP
HIC
LOG
SAMPLE ORFIELD TEST
GAP gINT FN. F01dRL3
CLIENT:
PROJECT:
LOCATION:
JOB NO:
DATE: 8/5/17
DATE: 12/6/17
This report of borehole must be read in conjunction with accompanying notes and abbreviations. It has been prepared forgeotechnical purposes only, without attempt to assess possible contamination. Any references to potential contamination are for
information only and do not necessarily indicate the presence or absence of soil or groundwater contamination.
REPORT OF BOREHOLE: BH027
Defence
Scherger PSI
Weipa
1669283
COORDS: 614820.8 m E 8604848.4 m N MGA94 56
SURFACE RL: 22.30 m DATUM: AHD
INCLINATION: -90°
HOLE DIA: 125 mm HOLE DEPTH: 13.50 m
DRILL RIG:
CONTRACTOR: Saxon Drilling
LOGGED: BJV
CHECKED: ELC
GA
P 8
_15.
0 LI
B.G
LB L
og G
AP
NO
N-C
OR
ED
FU
LL P
AG
E 1
6692
83.
GP
J <
<D
raw
ingF
ile>
> 2
7/07
/201
7 13
:50
8.3
0.00
4 D
atge
l Too
ls
MO
IST
UR
EC
ON
DIT
ION
CO
NS
IST
EN
CY
DE
NS
ITY PIEZOMETER DETAILS
0
5
10
15
20
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX G Data Validation
Number of Primary Samples: Number of Triplicate Samples:Number of Duplicate Samples: Number of Other QAQC Samples:
TypeMB
FB
RB
RB
RB
RB
RB
RB
RB
RBRB
Sample ID
-
Analyte Group Primary ID Duplicate IDPer- and polyfluoroalkyl substances (PFAS)
1218_SD004_0.0_170504 1218_QC102_170504
Per- and polyfluoroalkyl substances (PFAS)
1218_W002_S_170504 1218_QC103_S_170504
Per- and polyfluoroalkyl substances (PFAS)
1218_SW009_S_170505 1218_QC101_170505
Per- and polyfluoroalkyl substances (PFAS)
1218_BH024_8.5-8.75_170512 1218_QC107_170512
Per- and polyfluoroalkyl substances (PFAS)
1218_MW022_S_170515 1218_QC110_170515
Per- and polyfluoroalkyl substances (PFAS)
1218_BH022_11.5-11.75_170511 1218_QC108_170513
Per- and polyfluoroalkyl substances (PFAS)
1218_BH027_7.8-8.0_170508 1218_QC104_170509
Analyte Group Primary ID Triplicate IDPer- and polyfluoroalkyl substances (PFAS)
1218_BH022_11.5-11.75_170511 1218_QC208_170513
Per- and polyfluoroalkyl substances (PFAS)
1218_BH024_8.5-8.75_170512 1218_QC207_170512
Per- and polyfluoroalkyl substances (PFAS)
1218_MW022_S_170515 1218_QC210_170515
Analyte Group Analyte(s)
Note: Data validation assesses each analyte in terms of all the data validation variables and only the exceedances and outliers are reported in this form.
*When concentrations are less than the LOR for both primary and duplicate/triplicate results, no RPDs are calculated
Performed By: Bianca Vanzati Checked By: Erin CorbyDate: 23/05/2017 Date: 5/06/2017
Method Blank
Analyte
All results are below the LOR. Lab report EB1709386.
All results are below the LOR. Lab report EB1710297
All results are below the LOR. Lab report EB1710297
All results are below the LOR. Lab report EB1710297
All results are below the LOR. Lab report EB1710297
This batch has been validated and is considered suitable for environmental interpretive use.
Subcontractor Laboratory: ALS (Sydney) Work order Number: EB1709388, EB1709387, EB1709386Date Sampled: Sample Medium: Soil and Water
Samples analysed within appropriate holding times? Yes All ALS and Eurofins samples were analysed within appropriate holding times.
Sample IDAll results are below the LOR. Lab report EB1709386, EB1709387, EB1709388, EB1710297, 546883-S
Comments
Comments
Sample volumes sufficient for QC analysis?
Analyte Group
No surrogate recovery outliers occurred for lab report EB1709386, EB1709387, EB1709388
Comments
1218_QC309_170515 Perfluorooctane sulfonic acid (PFOS) above LOR (0.003 µg/L). Lab reprot EB1710297
All laboratory duplicate RPDs are within the laboratory based data quality objectives, lab report EB1709386, EB1709387, EB1709388, EB1710297, 546883-S
-
Matrix spike for perfluorooctanesulfonic acid (PFOS) failed for lab report 546883-S as the matrix spike recovery is outside of the recommended acceptance criteria. An acceptable recovery was obtained for the laboratory control sample indicating a sample matrix interference.
All results are below the LOR. Lab report EB1709388
-
1218_QC301_170504
All matrix spike recoveries are within the laboratory based data quality objectives, lab report EB1709386, EB1709387, EB1709388, EB1710297
Laboratory Duplicates (LD) Analyses
The field duplicate RPDs are within the data quality objectives for report 546883-S.
The field duplicate RPDs are within the data quality objectives for report EB1710297.
The field duplicate RPDs are within the data quality objectives for report EB1710297.
The field duplicate RPDs are within the data quality objectives for report 546883-W.
The field duplicate RPDs are within the data quality objectives for report EB1709387.
Comments
The field duplicate RPDs are within the data quality objectives for report EB1709386.
The field duplicate RPDs are within the data quality objectives for report EB1710297.
The field duplicate RPDs are within the data quality objectives for report 546883-S.
1218_QC401_170505
Comments
Not collected as part of this program
Perfluorooctane sulfonic acid (PFOS) above LOR (0.003 µg/L). Lab reprot EB1710297
All results are below the LOR. Lab report EB1709387
All results are below the LOR. Lab report EB1710297
1218_QC302_S_170505
1218_QC307_170511
1218_QC308_170512
1218_QC303_170508
1218_QC304_170509
1218_QC305_170510
1218_QC306_170511
QAQC Sample Information (Method Blank - MB, Rinsate Blank - RB, Field Blank - FB, Trip Blank - TB)
Yes All requested analyses on the COC performed.Signed by field staff and laboratory personnel. COC completed properly?
Yes No laboratory QC results for 546883-W Are there non-NATA accredited methods used? No
546883-S, 546883-W
04 to 15 May 2017
YesAll requested analysis completed?Samples received intact and chilled? Yes
Chromatograms supplied as appropriate? N/A N/A.
Laboratory QAQC recoveries within the laboratory based data quality objectives, with the exception of matrix spike for perfluorooctanesulfonic acid (PFOS) failed for lab report 546883-S as the matrix spike recovery is outside of the recommended acceptance criteria. An acceptable recovery was obtained for the laboratory control sample indicating a sample matrix interference.
Field Triplicates (FT) Analyses
DATA VALIDATION SUMMARY SHEET (Sydney)
4 Soil and 3 Water 9 rinsate and 1 field blank
Documentation and Sample Handling Information
Sample Information28 soil and 18 water 2 Soil and 1 Water
Y/N Comments
Project Name: PSI Cat 2 RAAF Base Scherger Project Number: 1669283
Primary Laboratory: ALS (Brisbane) Work order Number: EB1709388, EB1709387, EB1709386, EB1710297
Secondary Laboratory: Eurofins (Brisbane) Work order Number:
All field duplicate RPDs are within the data quality objectives, all method blanks, rinsate and field blanks below LOR.
The field duplicate RPDs are within the data quality objectives for report EB1710297.
PFOS was detected in rinsate water samples QC305 and QC309 (0.003 ug/L respectively). QC305 was collected from auger wash water after drilling BH023 on 10/05/2017. QC309 was collected from dip meter wash water after sampling new groundwater wells on 15/05/2017.
Laboratory reports signed by authorised personnel? Yes All reports signed.
Trip Spike Information
Analyte Control Spike Concentrations Trip Spike Concentration % Recovery
Perfluorooctanesulfonic acid (PFOS)
- All laboratory control spike recoveries for ALS are within the laboratory based data quality objectives, lab report EB1709386, EB1709387, EB1710297, 546883-S, 546883-W EB1709388
Matrix Spike (MS) AnalysesAnalyte Comments
Laboratory Control Spike (LCS) Analyses
Comments
Comments
Field Duplicates (FD) Analyses
The field duplicate RPDs are within the data quality objectives for report EB1709388.
Surrogate Compound Monitoring Analyses
Overall Comments
Golder Associates Pty Ltd
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DV
Page 1of 1
QAQC Analytical Results ‐ Rinsate and Trip Blanks
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283
Lab Report Number EB1709388 EB1709386 EB1709387 EB1710297 EB1710297 EB1710297 EB1710297 EB1710297 EB1710297 EB1710297
Field ID 1218_QC401_170505 1218_QC301_170504 1218_QC302_S_170505 1218_QC309_170515 1218_QC307_170511 1218_QC308_170512 1218_QC303_170508 1218_QC304_170509 1218_QC305_170510 1218_QC306_170511
Sampled Date 5/05/2017 4/05/2017 4/05/2017 15/05/2017 12/05/2017 13/05/2017 8/05/2017 9/05/2017 10/05/2017 13/05/2017
Sample Type Field_B Rinsate Rinsate Rinsate Rinsate Rinsate Rinsate Rinsate Rinsate Rinsate
ChemName Units LORN‐Methyl PFO sulfonamidoethanol (MeFOSE) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
Perfluorodecane sulfonic acid (PFDS) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorooctanoic Acid (PFOA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorooctane sulfonic acid (PFOS) µg/L 0.002 <0.002 <0.002 <0.002 0.003 <0.002 <0.002 <0.002 <0.002 0.003 <0.002
Perfluorohexane sulfonic acid (PFHxS) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Sum of PFHxS and PFOS (calculated) µg/L 0.002 <0.002 <0.002 <0.002 0.003 <0.002 <0.002 <0.002 <0.002 0.003 <0.002
PFAS (Sum of total ‐ Lab Reported) µg/L 0.002 <0.002 <0.002 <0.002 0.003 <0.002 <0.002 <0.002 <0.002 0.003 <0.002
Sum of PFAS (Swedish 11 + 8:2FTSA, lab reported) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorobutanoic acid (PFBA) µg/L 0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01
Perfluorohexanoic acid (PFHxA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluoroheptanoic acid (PFHpA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorodecanoic acid (PFDA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluoropentanoic acid (PFPeA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorononanoic acid (PFNA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorotetradecanoic acid (PFTeDA) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
Perfluorotridecanoic acid (PFTrDA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorododecanoic acid (PFDoDA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluoroundecanoic acid (PFUnDA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluoroheptane sulfonic acid (PFHpS) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluoropentane sulfonic acid (PFPeS) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
Perfluorobutane sulfonic acid (PFBS) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
N‐Ethyl PFO sulfonamide (EtFOSA) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
N‐Methyl PFO sulfonamide (MeFOSA) µg/L 0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005
Perfluorooctane sulfonamide (FOSA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) µg/L 0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002
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21/06/2017
RPD Results
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283
Sample Type Primary Field Duplicate RPD
Field ID 1218_SW009_S_170505 1218_QC101_170505 Primary vs Duplicate
Sampled Date 5/05/2017 5/05/2017
Lab Report Number EB1709388 EB1709388
ChemName Units LORN‐Methyl PFO sulfonamidoethanol (MeFOSE) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
Perfluorodecane sulfonic acid (PFDS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 ND
Perfluorooctanoic Acid (PFOA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorooctane sulfonic acid (PFOS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorohexane sulfonic acid (PFHxS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Sum of PFHxS and PFOS (calculated) µg/L 0.002 <0.002 <0.002 ND
PFAS (Sum of total ‐ Lab Reported) µg/L 0.002 <0.002 <0.002 ND
Sum of PFAS (Swedish 11 + 8:2FTSA, lab reported) µg/L 0.002 <0.002 <0.002 ND
Perfluorobutanoic acid (PFBA) µg/L 0.01 : 0.05 (Interlab) <0.01 <0.01 ND
Perfluorohexanoic acid (PFHxA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoroheptanoic acid (PFHpA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorodecanoic acid (PFDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoropentanoic acid (PFPeA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorononanoic acid (PFNA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorotetradecanoic acid (PFTeDA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
Perfluorotridecanoic acid (PFTrDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorododecanoic acid (PFDoDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoroundecanoic acid (PFUnDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoroheptane sulfonic acid (PFHpS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoropentane sulfonic acid (PFPeS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorobutane sulfonic acid (PFBS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
N‐Ethyl PFO sulfonamide (EtFOSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
N‐Methyl PFO sulfonamide (MeFOSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
Perfluorooctane sulfonamide (FOSA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 ND
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 ND
LegendND = Not Detected (RPDs not calculated if both primary and duplicate results are below LOR)
- = Not analysed/calculated
Acceptable RPDs:
RPD: ANY, Analysis result < 10 times LOR
RPD <= 50%, Analysis result >= 10 times LOR and < 20 times LOR
RPD <= 30%, Analysis result >= 20 times LOR
Indicates RPD result does not meet the acceptable criteria
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21/06/2017
RPD Results
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283Sample Type Primary Field Duplicate RPD
Field ID 1218_SD004_0.0_170504 1218_QC102_170504 Primary vs Duplicate
Sampled Date 4/05/2017 4/05/2017
Lab Report Number EB1709386 EB1709386
ChemName Units LOR
N‐Methyl PFO sulfonamidoethanol (MeFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
Perfluorodecane sulfonic acid (PFDS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 ND
Perfluorooctanoic Acid (PFOA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorooctane sulfonic acid (PFOS) mg/kg 0.0002 : 0.005 (Interlab) 0.0006 0.001 50
Perfluorohexane sulfonic acid (PFHxS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
PFAS (Sum of total ‐ Lab Reported) mg/kg 0.0002 0.0006 0.001 50
Perfluorobutanoic acid (PFBA) mg/kg 0.001 : 0.005 (Interlab) <0.001 <0.001 ND
Perfluorohexanoic acid (PFHxA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoroheptanoic acid (PFHpA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorodecanoic acid (PFDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoropentanoic acid (PFPeA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorononanoic acid (PFNA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorotetradecanoic acid (PFTeDA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
Perfluorotridecanoic acid (PFTrDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorododecanoic acid (PFDoDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoroundecanoic acid (PFUnDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoroheptane sulfonic acid (PFHpS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoropentane sulfonic acid (PFPeS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorobutane sulfonic acid (PFBS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) mg/kg 0.0005 : 0.01 (Interlab) <0.0005 <0.0005 ND
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
N‐Ethyl PFO sulfonamide (EtFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
N‐Methyl PFO sulfonamide (MeFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
Perfluorooctane sulfonamide (FOSA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 ND
LegendND = Not Detected (RPDs not calculated if both primary and duplicate results are below LOR)
- = Not analysed/calculated
Acceptable RPDs:
RPD: ANY, Analysis result < 10 times LOR
RPD <= 50%, Analysis result >= 10 times LOR and < 20 times LOR
RPD <= 30%, Analysis result >= 20 times LOR
Indicates RPD result does not meet the acceptable criteria
Per‐ and polyfluoroalkyl substances (PFAS)
Page 2 of 7
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21/06/2017
RPD Results
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283
Sample Type Primary Field Duplicate RPD
Field ID 1218_W002_S_170504 1218_QC103_S_170504 Primary vs Duplicate
Sampled Date 4/05/2017 4/05/2017
Lab Report Number EB1709387 EB1709387
ChemName Units LORN‐Methyl PFO sulfonamidoethanol (MeFOSE) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
Perfluorodecane sulfonic acid (PFDS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 ND
Perfluorooctanoic Acid (PFOA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorooctane sulfonic acid (PFOS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorohexane sulfonic acid (PFHxS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Sum of PFHxS and PFOS (calculated) µg/L 0.002 <0.002 <0.002 ND
PFAS (Sum of total ‐ Lab Reported) µg/L 0.002 <0.002 <0.002 ND
Sum of PFAS (Swedish 11 + 8:2FTSA, lab reported) µg/L 0.002 <0.002 <0.002 ND
Perfluorobutanoic acid (PFBA) µg/L 0.01 : 0.05 (Interlab) <0.01 <0.01 ND
Perfluorohexanoic acid (PFHxA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoroheptanoic acid (PFHpA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorodecanoic acid (PFDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoropentanoic acid (PFPeA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorononanoic acid (PFNA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorotetradecanoic acid (PFTeDA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
Perfluorotridecanoic acid (PFTrDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorododecanoic acid (PFDoDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoroundecanoic acid (PFUnDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoroheptane sulfonic acid (PFHpS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluoropentane sulfonic acid (PFPeS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
Perfluorobutane sulfonic acid (PFBS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 ND
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 ND
N‐Ethyl PFO sulfonamide (EtFOSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
N‐Methyl PFO sulfonamide (MeFOSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 ND
Perfluorooctane sulfonamide (FOSA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 ND
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 ND
LegendND = Not Detected (RPDs not calculated if both primary and duplicate results are below LOR)
- = Not analysed/calculated
Acceptable RPDs:
RPD: ANY, Analysis result < 10 times LOR
RPD <= 50%, Analysis result >= 10 times LOR and < 20 times LOR
RPD <= 30%, Analysis result >= 20 times LOR
Indicates RPD result does not meet the acceptable criteria
Page 3 of 7
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21/06/2017
RPD Results
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283
Sample Type Primary Field Duplicate RPD
Field ID 1218_BH027_7.8‐8.0_170508 1218_QC104_170509 Primary vs Duplicate
Sampled Date 8/05/2017 8/05/2017
Lab Report Number EB1710297 EB1710297
ChemName Units LOR
N‐Methyl PFO sulfonamidoethanol (MeFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
Perfluorodecane sulfonic acid (PFDS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 ND
Perfluorooctanoic Acid (PFOA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorooctane sulfonic acid (PFOS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorohexane sulfonic acid (PFHxS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
PFAS (Sum of total ‐ Lab Reported) mg/kg 0.0002 <0.0002 <0.0002 ND
Perfluorobutanoic acid (PFBA) mg/kg 0.001 : 0.005 (Interlab) <0.001 <0.001 ND
Perfluorohexanoic acid (PFHxA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoroheptanoic acid (PFHpA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorodecanoic acid (PFDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoropentanoic acid (PFPeA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorononanoic acid (PFNA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorotetradecanoic acid (PFTeDA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
Perfluorotridecanoic acid (PFTrDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorododecanoic acid (PFDoDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoroundecanoic acid (PFUnDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoroheptane sulfonic acid (PFHpS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluoropentane sulfonic acid (PFPeS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
Perfluorobutane sulfonic acid (PFBS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) mg/kg 0.0005 : 0.01 (Interlab) <0.0005 <0.0005 ND
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
N‐Ethyl PFO sulfonamide (EtFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
N‐Methyl PFO sulfonamide (MeFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 ND
Perfluorooctane sulfonamide (FOSA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 ND
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 ND
LegendND = Not Detected (RPDs not calculated if both primary and duplicate results are below LOR)
- = Not analysed/calculated
Acceptable RPDs:
RPD: ANY, Analysis result < 10 times LOR
RPD <= 50%, Analysis result >= 10 times LOR and < 20 times LOR
RPD <= 30%, Analysis result >= 20 times LOR
Indicates RPD result does not meet the acceptable criteria
Per‐ and polyfluoroalkyl substances (PFAS)
Page 4 of 7
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21/06/2017
RPD Results
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283
Sample Type Primary Field Duplicate Field Triplicate
Field ID 1218_BH024_8.5‐8.75_170512 1218_QC107_170512 1218_QC207_170512
Sampled Date 12/05/2017 12/05/2017 12/05/2017
Lab Report Number EB1710297 EB1710297 546883‐S
ChemName Units LOR
N‐Methyl PFO sulfonamidoethanol (MeFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
Perfluorodecane sulfonic acid (PFDS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 <0.01 ND ND
Perfluorooctanoic Acid (PFOA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorooctane sulfonic acid (PFOS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorohexane sulfonic acid (PFHxS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
PFAS (Sum of total ‐ Lab Reported) mg/kg 0.0002 <0.0002 <0.0002 ‐ ND ND
Perfluorobutanoic acid (PFBA) mg/kg 0.001 : 0.005 (Interlab) <0.001 <0.001 <0.005 ND ND
Perfluorohexanoic acid (PFHxA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoroheptanoic acid (PFHpA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorodecanoic acid (PFDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoropentanoic acid (PFPeA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorononanoic acid (PFNA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorotetradecanoic acid (PFTeDA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.05 ND ND
Perfluorotridecanoic acid (PFTrDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorododecanoic acid (PFDoDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoroundecanoic acid (PFUnDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoroheptane sulfonic acid (PFHpS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoropentane sulfonic acid (PFPeS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorobutane sulfonic acid (PFBS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) mg/kg 0.0005 : 0.01 (Interlab) <0.0005 <0.0005 <0.01 ND ND
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
N‐Ethyl PFO sulfonamide (EtFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
N‐Methyl PFO sulfonamide (MeFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
Perfluorooctane sulfonamide (FOSA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 <0.01 ND ND
LegendND = Not Detected (RPDs not calculated if both primary and duplicate results are below LOR)
- = Not analysed/calculated
Acceptable RPDs:
RPD: ANY, Analysis result < 10 times LOR
RPD <= 50%, Analysis result >= 10 times LOR and < 20 times LOR
RPD <= 30%, Analysis result >= 20 times LOR
Indicates RPD result does not meet the acceptable criteria
Per‐ and polyfluoroalkyl substances (PFAS)
RPDs
Primary vs Duplicate
Primary vs Inter Duplicate
Page 5 of 7
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21/06/2017
RPD Results
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283
Sample Type Primary Field Duplicate Field Triplicate
Field ID 1218_BH022_11.5‐11.75_170511 1218_QC108_170513 1218_QC208_170513
Sampled Date 13/05/2017 13/05/2017 13/05/2017
Lab Report Number EB1710297 EB1710297 546883‐S
ChemName Units LOR
N‐Methyl PFO sulfonamidoethanol (MeFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
Perfluorodecane sulfonic acid (PFDS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 <0.01 ND ND
Perfluorooctanoic Acid (PFOA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorooctane sulfonic acid (PFOS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorohexane sulfonic acid (PFHxS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
PFAS (Sum of total ‐ Lab Reported) mg/kg 0.0002 <0.0002 <0.0002 ‐ ND ‐
Perfluorobutanoic acid (PFBA) mg/kg 0.001 : 0.005 (Interlab) <0.001 <0.001 <0.005 ND ND
Perfluorohexanoic acid (PFHxA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoroheptanoic acid (PFHpA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorodecanoic acid (PFDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoropentanoic acid (PFPeA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorononanoic acid (PFNA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorotetradecanoic acid (PFTeDA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.05 ND ND
Perfluorotridecanoic acid (PFTrDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorododecanoic acid (PFDoDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoroundecanoic acid (PFUnDA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoroheptane sulfonic acid (PFHpS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluoropentane sulfonic acid (PFPeS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
Perfluorobutane sulfonic acid (PFBS) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) mg/kg 0.0005 : 0.01 (Interlab) <0.0005 <0.0005 <0.01 ND ND
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
N‐Ethyl PFO sulfonamide (EtFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
N‐Methyl PFO sulfonamide (MeFOSA) mg/kg 0.0005 : 0.005 (Interlab) <0.0005 <0.0005 <0.005 ND ND
Perfluorooctane sulfonamide (FOSA) mg/kg 0.0002 : 0.005 (Interlab) <0.0002 <0.0002 <0.005 ND ND
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) mg/kg 0.0002 : 0.01 (Interlab) <0.0002 <0.0002 <0.01 ND ND
LegendND = Not Detected (RPDs not calculated if both primary and duplicate results are below LOR)
- = Not analysed/calculated
Acceptable RPDs:
RPD: ANY, Analysis result < 10 times LOR
RPD <= 50%, Analysis result >= 10 times LOR and < 20 times LOR
RPD <= 30%, Analysis result >= 20 times LOR
Indicates RPD result does not meet the acceptable criteria
Per‐ and polyfluoroalkyl substances (PFAS)
RPDs
Primary vs Duplicate
Primary vs Inter Duplicate
Page 6 of 7
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21/06/2017
RPD Results
PSI Cat 2 RAAF Base Scherger (1218) Weipa
Project: 1669283
Sample Typre Primary Field Duplicate Field Triplicate
Field ID 1218_MW022_S_170515 1218_QC110_170515 1218_QC210_170515
Sampled Date 15/05/2017 15/05/2017 15/05/2017
Lab Report Number EB1710297 EB1710297 546883‐W
ChemName Units LOR
N‐Methyl PFO sulfonamidoethanol (MeFOSE) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 <0.05
Perfluorodecane sulfonic acid (PFDS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
N‐methyl‐PFO sulfonamidoacetic acid (MeFOSAA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 <0.05 ND ND
Perfluorooctanoic Acid (PFOA) µg/L 0.002 : 0.01 (Interlab) 0.002 0.002 <0.01 ND ND
Perfluorooctane sulfonic acid (PFOS) µg/L 0.002 : 0.01 (Interlab) 0.008 0.009 0.01 12% 22%
Perfluorohexane sulfonic acid (PFHxS) µg/L 0.002 : 0.01 (Interlab) 0.008 0.009 <0.01 12% ND
Sum of PFHxS and PFOS (calculated) µg/L 0.002 0.016 0.018 ‐ 12% ND
PFAS (Sum of total ‐ Lab Reported) µg/L 0.002 0.034 0.036 ‐ 6% ‐
Sum of PFAS (Swedish 11 + 8:2FTSA, lab reported) µg/L 0.002 0.026 0.027 ‐ 4% ND
Perfluorobutanoic acid (PFBA) µg/L 0.01 : 0.05 (Interlab) <0.01 <0.01 <0.05 ND ND
Perfluorohexanoic acid (PFHxA) µg/L 0.002 : 0.01 (Interlab) 0.008 0.009 <0.01 12% ND
Perfluoroheptanoic acid (PFHpA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
Perfluorodecanoic acid (PFDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
Perfluoropentanoic acid (PFPeA) µg/L 0.002 : 0.01 (Interlab) 0.003 0.002 <0.01 40% ND
Perfluorononanoic acid (PFNA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
Perfluorotetradecanoic acid (PFTeDA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 <0.01 ND ND
Perfluorotridecanoic acid (PFTrDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
Perfluorododecanoic acid (PFDoDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
Perfluoroundecanoic acid (PFUnDA) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
Perfluoroheptane sulfonic acid (PFHpS) µg/L 0.002 : 0.01 (Interlab) <0.002 <0.002 <0.01 ND ND
Perfluoropentane sulfonic acid (PFPeS) µg/L 0.002 : 0.01 (Interlab) 0.002 0.002 <0.01 ND ND
Perfluorobutane sulfonic acid (PFBS) µg/L 0.002 : 0.01 (Interlab) 0.003 0.003 <0.01 ND ND
4:2 Fluorotelomer sulfonic acid (4:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 <0.01 ND ND
6:2 Fluorotelomer sulfonic acid (6:2 FTSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 <0.05 ND ND
8:2 Fluorotelomer sulfonic acid (8:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 <0.01 ND ND
10:2 Fluorotelomer sulfonic acid (10:2 FTSA) µg/L 0.005 : 0.01 (Interlab) <0.005 <0.005 <0.01 ND ND
N‐Ethyl PFO sulfonamide (EtFOSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 <0.05 ND ND
N‐Ethyl PFO sulfonamidoethanol (EtFOSE) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 <0.05 ND ND
N‐Methyl PFO sulfonamide (MeFOSA) µg/L 0.005 : 0.05 (Interlab) <0.005 <0.005 <0.05 ND ND
Perfluorooctane sulfonamide (FOSA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 <0.05 ND ND
N‐ethyl‐PFO sulfonamidoacetic acid (EtFOSAA) µg/L 0.002 : 0.05 (Interlab) <0.002 <0.002 <0.05 ND ND
LegendND = Not Detected (RPDs not calculated if both primary and duplicate results are below LOR)
- = Not analysed/calculated
Acceptable RPDs:
RPD: ANY, Analysis result < 10 times LOR
RPD <= 50%, Analysis result >= 10 times LOR and < 20 times LOR
RPD <= 30%, Analysis result >= 20 times LOR
Indicates RPD result does not meet the acceptable criteria
RPDs
Primary vs Duplicate
Primary vs Inter Duplicate
Per‐ and polyfluoroalkyl substances (PFAS)
Page 7 of 7
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21/06/2017
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX H Laboratory Certificates
.Company Name: Golder Associates Pty Ltd (Qld) Order No.: Received: May 19, 2017 2:45 PMAddress: 147 Coronation Dve Report #: 546883 Due: May 26, 2017
Milton Phone: (07) 3721 5400 Priority: 5 DayQLD 4064 Fax: (07) 3721 5401 Contact Name: Fran Mitchell
Project Name:Project ID: 1669283
Eurofins | mgt Analytical Services Manager : Ryan Gilbert
Sample Detail
Moisture S
et
Per- and P
olyfluorinated Alkyl S
ubstances(P
FA
Ss)
Melbourne Laboratory - NATA Site # 1254 & 14271
Sydney Laboratory - NATA Site # 18217
Brisbane Laboratory - NATA Site # 20794 X X
Perth Laboratory - NATA Site # 18217
External Laboratory
No Sample ID Sample Date SamplingTime
Matrix LAB ID
1 1218_QC208_170513
May 13, 2017 Soil B17-My19667 X X
2 1218_QC207_170512
May 12, 2017 Soil B17-My19668 X X
3 1218_QC210_170515
May 15, 2017 Water B17-My19669 X
Test Counts 2 3
ABN– 50 005 085 521e.mail : [email protected] : www.eurofins.com.au
MelbourneMelbourneMelbourneMelbourne2-5 Kingston Town CloseOakleigh VIC 3166Phone : +61 3 8564 5000NATA # 1261Site # 1254 & 14271
SydneySydneySydneySydneyUnit F3, Building F16 Mars RoadLane Cove West NSW 2066Phone : +61 2 9900 8400NATA # 1261 Site # 18217
BrisbaneBrisbaneBrisbaneBrisbane1/21 Smallwood PlaceMurarrie QLD 4172Phone : +61 7 3902 4600NATA # 1261 Site # 20794
PerthPerthPerthPerth2/91 Leach HighwayKewdale WA 6105Phone : +61 8 9251 9600NATA # 1261Site # 18217
Certificate of Analysis
Golder Associates Pty Ltd
147 Coronation Dve
Milton
QLD 4064
Attention: Bianca Vanzati
Report 546883-S
Project name
Project ID 1669283
Received Date May 19, 2017
Client Sample ID 1218_QC208_170513
1218_QC207_170512
Sample Matrix Soil Soil
Eurofins | mgt Sample No. B17-My19667 B17-My19668
Date Sampled May 13, 2017 May 12, 2017
Test/Reference LOR Unit
Perfluoroalkyl carboxylic acids (PFCAs)
Perfluorobutanoic acid (PFBA) 5 ug/kg < 5 < 5
Perfluoropentanoic acid (PFPeA) 5 ug/kg < 5 < 5
Perfluorohexanoic acid (PFHxA) 5 ug/kg < 5 < 5
Perfluoroheptanoic acid (PFHpA) 5 ug/kg < 5 < 5
Perfluorooctanoic acid (PFOA) 5 ug/kg < 5 < 5
Perfluorononanoic acid (PFNA) 5 ug/kg < 5 < 5
Perfluorodecanoic acid (PFDA) 5 ug/kg < 5 < 5
Perfluoroundecanoic acid (PFUnA) 5 ug/kg < 5 < 5
Perfluorododecanoic acid (PFDoA) 5 ug/kg < 5 < 5
Perfluorotridecanoic acid (PFTrDA) 5 ug/kg < 5 < 5
Perfluorotetradecanoic acid (PFTeDA) 5 ug/kg < 50 < 50
13C4-PFBA (surr.) 1 % 116 94
13C5-PFPeA (surr.) 1 % 124 95
13C5-PFHxA (surr.) 1 % 134 110
13C4-PFHpA (surr.) 1 % 130 109
13C8-PFOA (surr.) 1 % 129 107
13C5-PFNA (surr.) 1 % 127 106
13C6-PFDA (surr.) 1 % 127 104
13C2-PFUnDA (surr.) 1 % 116 85
13C2-PFDoDA (surr.) 1 % 92 52
13C2-PFTeDA (surr.) 1 % INT INT
Perfluoroalkane sulfonamides (PFASAs)
Perfluorooctane sulfonamide (FOSA) 5 ug/kg < 5 < 5
N-methylperfluoro-1-octane sulfonamide (N-MeFOSA) 5 ug/kg < 5 < 5
N-ethylperfluoro-1-octane sulfonamide (N-EtFOSA) 5 ug/kg < 5 < 5
2-(N-methylperfluoro-1-octane sulfonamido)-ethanol(N-MeFOSE) 5 ug/kg < 5 < 5
2-(N-ethylperfluoro-1-octane sulfonamido)-ethanol (N-EtFOSE) 5 ug/kg < 5 < 5
N-ethyl-perfluorooctanesulfonamidoacetic acid (N-EtFOSAA) 10 ug/kg < 10 < 10
N-methyl-perfluorooctanesulfonamidoacetic acid (N-MeFOSAA) 10 ug/kg < 10 < 10
13C8-FOSA (surr.) 1 % 107 97
D3-N-MeFOSA (surr.) 1 % 93 68
D5-N-EtFOSA (surr.) 1 % 91 51
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 1 of 10
Report Number: 546883-S
NATA AccreditedAccreditation Number 1261Site Number 20794
Accredited for compliance with ISO/IEC 17025 – TestingThe results of the tests, calibrations and/ormeasurements included in this document are traceableto Australian/national standards.
Client Sample ID 1218_QC208_170513
1218_QC207_170512
Sample Matrix Soil Soil
Eurofins | mgt Sample No. B17-My19667 B17-My19668
Date Sampled May 13, 2017 May 12, 2017
Test/Reference LOR Unit
Perfluoroalkane sulfonamides (PFASAs)
D7-N-MeFOSE (surr.) 1 % 94 73
D9-N-EtFOSE (surr.) 1 % 85 60
D5-N-EtFOSAA (surr.) 1 % 100 73
D3-N-MeFOSAA (surr.) 1 % 112 87
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs)
Perfluorobutanesulfonic acid (PFBS) 5 ug/kg < 5 < 5
Perfluoropentanesulfonic acid (PFPeS) 5 ug/kg < 5 < 5
Perfluorohexanesulfonic acid (PFHxS) 5 ug/kg < 5 < 5
Perfluoroheptanesulfonic acid (PFHpS) 5 ug/kg < 5 < 5
Perfluorooctanesulfonic acid (PFOS)N11 5 ug/kg < 5 < 5
Perfluorodecanesulfonic acid (PFDS) 5 ug/kg < 5 < 5
13C3-PFBS (surr.) 1 % 130 111
18O2-PFHxS (surr.) 1 % 127 111
13C8-PFOS (surr.) 1 % 136 108
n:2 Fluorotelomer sulfonic acids
1H.1H.2H.2H-perfluorohexanesulfonic acid (4:2 FTS) 5 ug/kg < 5 < 5
1H.1H.2H.2H-perfluorooctanesulfonic acid (6:2 FTS) 10 ug/kg < 10 < 10
1H.1H.2H.2H-perfluorodecanesulfonic acid (8:2 FTS) 5 ug/kg < 5 < 5
1H.1H.2H.2H-perfluorododecanesulfonic acid (10:2FTS) 5 ug/kg < 5 < 5
13C2-4:2 FTS (surr.) 1 % 119 113
13C2-6:2 FTS (surr.) 1 % 121 105
13C2-8:2 FTS (surr.) 1 % 131 119
% Moisture 1 % 12 8.9
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 2 of 10
Report Number: 546883-S
Sample HistoryWhere samples are submitted/analysed over several days, the last date of extraction and analysis is reported.A recent review of our LIMS has resulted in the correction or clarification of some method identifications. Due to this, some of the method reference information on reports has changed. However,no substantive change has been made to our laboratory methods, and as such there is no change in the validity of current or previous results (regarding both quality and NATA accreditation).
If the date and time of sampling are not provided, the Laboratory will not be responsible for compromised results should testing be performed outside the recommended holding time.
Description Testing Site Extracted Holding Time
Per- and Polyfluorinated Alkyl Substances (PFASs)
Perfluoroalkyl carboxylic acids (PFCAs) Brisbane May 22, 2017 180 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
Perfluoroalkane sulfonamides (PFASAs) Brisbane May 22, 2017 180 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs) Brisbane May 22, 2017 180 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
n:2 Fluorotelomer sulfonic acids Brisbane May 22, 2017 180 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
% Moisture Brisbane May 19, 2017 14 Day
- Method: LTM-GEN-7080 Moisture
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 3 of 10
Report Number: 546883-S
.Company Name: Golder Associates Pty Ltd (Qld) Order No.: Received: May 19, 2017 2:45 PMAddress: 147 Coronation Dve Report #: 546883 Due: May 26, 2017
Milton Phone: (07) 3721 5400 Priority: 5 DayQLD 4064 Fax: (07) 3721 5401 Contact Name: Fran Mitchell
Project Name:Project ID: 1669283
Eurofins | mgt Analytical Services Manager : Ryan Gilbert
Sample Detail
Moisture S
et
Per- and P
olyfluorinated Alkyl S
ubstances(P
FA
Ss)
Melbourne Laboratory - NATA Site # 1254 & 14271
Sydney Laboratory - NATA Site # 18217
Brisbane Laboratory - NATA Site # 20794 X X
Perth Laboratory - NATA Site # 18217
External Laboratory
No Sample ID Sample Date SamplingTime
Matrix LAB ID
1 1218_QC208_170513
May 13, 2017 Soil B17-My19667 X X
2 1218_QC207_170512
May 12, 2017 Soil B17-My19668 X X
3 1218_QC210_170515
May 15, 2017 Water B17-My19669 X
Test Counts 2 3
ABN– 50 005 085 521e.mail : [email protected] : www.eurofins.com.au
MelbourneMelbourneMelbourneMelbourne2-5 Kingston Town CloseOakleigh VIC 3166Phone : +61 3 8564 5000NATA # 1261Site # 1254 & 14271
SydneySydneySydneySydneyUnit F3, Building F16 Mars RoadLane Cove West NSW 2066Phone : +61 2 9900 8400NATA # 1261 Site # 18217
BrisbaneBrisbaneBrisbaneBrisbane1/21 Smallwood PlaceMurarrie QLD 4172Phone : +61 7 3902 4600NATA # 1261 Site # 20794
PerthPerthPerthPerth2/91 Leach HighwayKewdale WA 6105Phone : +61 8 9251 9600NATA # 1261Site # 18217
Date Reported:Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 4 of 10
Report Number: 546883-S
Internal Quality Control Review and Glossary
General
Holding Times
Units
Terms
QC - Acceptance Criteria
QC Data General Comments
1. Laboratory QC results for Method Blanks, Duplicates, Matrix Spikes, and Laboratory Control Samples are included in this QC report where applicable. Additional QC data may be available on
request.
2. All soil results are reported on a dry basis, unless otherwise stated.
3. All biota results are reported on a wet weight basis on the edible portion, unless otherwise stated.
4. Actual LORs are matrix dependant. Quoted LORs may be raised where sample extracts are diluted due to interferences.
5. Results are uncorrected for matrix spikes or surrogate recoveries.
6. SVOC analysis on waters are performed on homogenised, unfiltered samples, unless noted otherwise.
7. Samples were analysed on an 'as received' basis.
8. This report replaces any interim results previously issued.
Please refer to 'Sample Preservation and Container Guide' for holding times (QS3001).
For samples received on the last day of holding time, notification of testing requirements should have been received at least 6 hours prior to sample receipt deadlines as stated on the Sample
Receipt Advice.
If the Laboratory did not receive the information in the required timeframe, and regardless of any other integrity issues, suitably qualified results may still be reported.
Holding times apply from the date of sampling, therefore compliance to these may be outside the laboratory's control.
**NOTE: pH duplicates are reported as a range NOT as RPD
mg/kg: milligrams per kilogram mg/L: milligrams per litre
ug/L: micrograms per litre ppm: Parts per million
ppb: Parts per billion %: Percentage
org/100mL: Organisms per 100 millilitres NTU: Nephelometric Turbidity Units
MPN/100mL: Most Probable Number of organisms per 100 millilitres
Dry Where a moisture has been determined on a solid sample the result is expressed on a dry basis.
LOR Limit of Reporting.
SPIKE Addition of the analyte to the sample and reported as percentage recovery.
RPD Relative Percent Difference between two Duplicate pieces of analysis.
LCS Laboratory Control Sample - reported as percent recovery.
CRM Certified Reference Material - reported as percent recovery.
Method Blank In the case of solid samples these are performed on laboratory certified clean sands.
In the case of water samples these are performed on de-ionised water.
Surr - Surrogate The addition of a like compound to the analyte target and reported as percentage recovery.
Duplicate A second piece of analysis from the same sample and reported in the same units as the result to show comparison.
Batch Duplicate A second piece of analysis from a sample outside of the clients batch of samples but run within the laboratory batch of analysis.
Batch SPIKE Spike recovery reported on a sample from outside of the clients batch of samples but run within the laboratory batch of analysis.
USEPA United States Environmental Protection Agency
APHA American Public Health Association
TCLP Toxicity Characteristic Leaching Procedure
COC Chain of Custody
SRA Sample Receipt Advice
CP Client Parent - QC was performed on samples pertaining to this report
NCP Non-Client Parent - QC performed on samples not pertaining to this report, QC is representative of the sequence or batch that client samples were analysed within.
TEQ Toxic Equivalency Quotient
RPD Duplicates: Global RPD Duplicates Acceptance Criteria is 30% however the following acceptance guidelines are equally applicable:
Results <10 times the LOR : No Limit
Results between 10-20 times the LOR : RPD must lie between 0-50%
Results >20 times the LOR : RPD must lie between 0-30%
Surrogate Recoveries: Recoveries must lie between 50-150%-Phenols & PFASs 20-130%
1. Where a result is reported as a less than (<), higher than the nominated LOR, this is due to either matrix interference, extract dilution required due to interferences or contaminant levels within
the sample, high moisture content or insufficient sample provided.
2. Duplicate data shown within this report that states the word "BATCH" is a Batch Duplicate from outside of your sample batch, but within the laboratory sample batch at a 1:10 ratio. The Parent
and Duplicate data shown is not data from your samples.
3. Organochlorine Pesticide analysis - where reporting LCS data, Toxaphene & Chlordane are not added to the LCS.
4. Organochlorine Pesticide analysis - where reporting Spike data, Toxaphene is not added to the Spike.
5. Total Recoverable Hydrocarbons - where reporting Spike & LCS data, a single spike of commercial Hydrocarbon products in the range of C12-C30 is added and it's Total Recovery is reported
in the C10-C14 cell of the Report.
6. pH and Free Chlorine analysed in the laboratory - Analysis on this test must begin within 30 minutes of sampling.Therefore laboratory analysis is unlikely to be completed within holding time.
Analysis will begin as soon as possible after sample receipt.
7. Recovery Data (Spikes & Surrogates) - where chromatographic interference does not allow the determination of Recovery the term "INT" appears against that analyte.
8. Polychlorinated Biphenyls are spiked only using Aroclor 1260 in Matrix Spikes and LCS.
9. For Matrix Spikes and LCS results a dash " -" in the report means that the specific analyte was not added to the QC sample.
10. Duplicate RPDs are calculated from raw analytical data thus it is possible to have two sets of data.
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 5 of 10
Report Number: 546883-S
Quality Control Results
Test Units Result 1 AcceptanceLimits
PassLimits
QualifyingCode
Method Blank
Perfluoroalkyl carboxylic acids (PFCAs)
Perfluorobutanoic acid (PFBA) ug/kg < 5 5 Pass
Perfluoropentanoic acid (PFPeA) ug/kg < 5 5 Pass
Perfluorohexanoic acid (PFHxA) ug/kg < 5 5 Pass
Perfluoroheptanoic acid (PFHpA) ug/kg < 5 5 Pass
Perfluorooctanoic acid (PFOA) ug/kg < 5 5 Pass
Perfluorononanoic acid (PFNA) ug/kg < 5 5 Pass
Perfluorodecanoic acid (PFDA) ug/kg < 5 5 Pass
Perfluoroundecanoic acid (PFUnA) ug/kg < 5 5 Pass
Perfluorododecanoic acid (PFDoA) ug/kg < 5 5 Pass
Perfluorotridecanoic acid (PFTrDA) ug/kg < 5 5 Pass
Perfluorotetradecanoic acid (PFTeDA) ug/kg < 5 5 Pass
Method Blank
Perfluoroalkane sulfonamides (PFASAs)
Perfluorooctane sulfonamide (FOSA) ug/kg < 5 5 Pass
N-methylperfluoro-1-octane sulfonamide (N-MeFOSA) ug/kg < 5 5 Pass
N-ethylperfluoro-1-octane sulfonamide (N-EtFOSA) ug/kg < 5 5 Pass
2-(N-methylperfluoro-1-octane sulfonamido)-ethanol (N-MeFOSE) ug/kg < 5 5 Pass
2-(N-ethylperfluoro-1-octane sulfonamido)-ethanol (N-EtFOSE) ug/kg < 5 5 Pass
N-ethyl-perfluorooctanesulfonamidoacetic acid (N-EtFOSAA) ug/kg < 10 10 Pass
N-methyl-perfluorooctanesulfonamidoacetic acid (N-MeFOSAA) ug/kg < 10 10 Pass
Method Blank
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs)
Perfluorobutanesulfonic acid (PFBS) ug/kg < 5 5 Pass
Perfluoropentanesulfonic acid (PFPeS) ug/kg < 5 5 Pass
Perfluorohexanesulfonic acid (PFHxS) ug/kg < 5 5 Pass
Perfluoroheptanesulfonic acid (PFHpS) ug/kg < 5 5 Pass
Perfluorooctanesulfonic acid (PFOS) ug/kg < 5 5 Pass
Perfluorodecanesulfonic acid (PFDS) ug/kg < 5 5 Pass
Method Blank
n:2 Fluorotelomer sulfonic acids
1H.1H.2H.2H-perfluorohexanesulfonic acid (4:2 FTS) ug/kg < 5 5 Pass
1H.1H.2H.2H-perfluorooctanesulfonic acid (6:2 FTS) ug/kg < 10 10 Pass
1H.1H.2H.2H-perfluorodecanesulfonic acid (8:2 FTS) ug/kg < 5 5 Pass
1H.1H.2H.2H-perfluorododecanesulfonic acid (10:2 FTS) ug/kg < 5 5 Pass
LCS - % Recovery
Perfluoroalkyl carboxylic acids (PFCAs)
Perfluorobutanoic acid (PFBA) % 101 50-150 Pass
Perfluoropentanoic acid (PFPeA) % 106 50-150 Pass
Perfluorohexanoic acid (PFHxA) % 101 50-150 Pass
Perfluoroheptanoic acid (PFHpA) % 100 50-150 Pass
Perfluorooctanoic acid (PFOA) % 104 50-150 Pass
Perfluorononanoic acid (PFNA) % 104 50-150 Pass
Perfluorodecanoic acid (PFDA) % 105 50-150 Pass
Perfluoroundecanoic acid (PFUnA) % 107 50-150 Pass
Perfluorododecanoic acid (PFDoA) % 108 50-150 Pass
Perfluorotridecanoic acid (PFTrDA) % 74 50-150 Pass
Perfluorotetradecanoic acid (PFTeDA) % 116 50-150 Pass
LCS - % Recovery
Perfluoroalkane sulfonamides (PFASAs)
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 6 of 10
Report Number: 546883-S
Test Units Result 1 AcceptanceLimits
PassLimits
QualifyingCode
Perfluorooctane sulfonamide (FOSA) % 105 50-150 Pass
N-methylperfluoro-1-octane sulfonamide (N-MeFOSA) % 115 50-150 Pass
N-ethylperfluoro-1-octane sulfonamide (N-EtFOSA) % 128 50-150 Pass
2-(N-methylperfluoro-1-octane sulfonamido)-ethanol (N-MeFOSE) % 111 50-150 Pass
2-(N-ethylperfluoro-1-octane sulfonamido)-ethanol (N-EtFOSE) % 107 50-150 Pass
N-ethyl-perfluorooctanesulfonamidoacetic acid (N-EtFOSAA) % 104 50-150 Pass
N-methyl-perfluorooctanesulfonamidoacetic acid (N-MeFOSAA) % 102 50-150 Pass
LCS - % Recovery
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs)
Perfluorobutanesulfonic acid (PFBS) % 110 50-150 Pass
Perfluoropentanesulfonic acid (PFPeS) % 108 50-150 Pass
Perfluorohexanesulfonic acid (PFHxS) % 112 50-150 Pass
Perfluoroheptanesulfonic acid (PFHpS) % 106 50-150 Pass
Perfluorooctanesulfonic acid (PFOS) % 104 50-150 Pass
Perfluorodecanesulfonic acid (PFDS) % 100 50-150 Pass
LCS - % Recovery
n:2 Fluorotelomer sulfonic acids
1H.1H.2H.2H-perfluorohexanesulfonic acid (4:2 FTS) % 110 50-150 Pass
1H.1H.2H.2H-perfluorooctanesulfonic acid (6:2 FTS) % 145 50-150 Pass
1H.1H.2H.2H-perfluorodecanesulfonic acid (8:2 FTS) % 110 50-150 Pass
1H.1H.2H.2H-perfluorododecanesulfonic acid (10:2 FTS) % 128 50-150 Pass
Test Lab Sample ID QASource Units Result 1 Acceptance
LimitsPass
LimitsQualifying
Code
Spike - % Recovery
Perfluoroalkyl carboxylic acids (PFCAs) Result 1
Perfluorobutanoic acid (PFBA) B17-My19667 CP % 112 50-150 Pass
Perfluoropentanoic acid (PFPeA) B17-My19667 CP % 111 50-150 Pass
Perfluorohexanoic acid (PFHxA) B17-My19667 CP % 111 50-150 Pass
Perfluoroheptanoic acid (PFHpA) B17-My19667 CP % 107 50-150 Pass
Perfluorooctanoic acid (PFOA) B17-My19667 CP % 110 50-150 Pass
Perfluorononanoic acid (PFNA) B17-My19667 CP % 114 50-150 Pass
Perfluorodecanoic acid (PFDA) B17-My19667 CP % 111 50-150 Pass
Perfluoroundecanoic acid (PFUnA) B17-My19667 CP % 108 50-150 Pass
Perfluorododecanoic acid (PFDoA) B17-My19667 CP % 139 50-150 Pass
Perfluorotridecanoic acid (PFTrDA) B17-My19667 CP % 54 50-150 Pass
Perfluorotetradecanoic acid(PFTeDA) B17-My19667 CP % 105 50-150 Pass
Spike - % Recovery
Perfluoroalkane sulfonamides (PFASAs) Result 1
Perfluorooctane sulfonamide(FOSA) S17-My22163 NCP % 112 50-150 Pass
N-methylperfluoro-1-octanesulfonamide (N-MeFOSA) S17-My22163 NCP % 116 50-150 Pass
N-ethylperfluoro-1-octanesulfonamide (N-EtFOSA) S17-My22163 NCP % 132 50-150 Pass
2-(N-methylperfluoro-1-octanesulfonamido)-ethanol (N-MeFOSE) S17-My22163 NCP % 117 50-150 Pass
2-(N-ethylperfluoro-1-octanesulfonamido)-ethanol (N-EtFOSE) S17-My22163 NCP % 110 50-150 Pass
N-ethyl-perfluorooctanesulfonamidoaceticacid (N-EtFOSAA) S17-My22163 NCP % 110 50-150 Pass
N-methyl-perfluorooctanesulfonamidoaceticacid (N-MeFOSAA) S17-My22163 NCP % 113 50-150 Pass
Spike - % Recovery
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs) Result 1
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 7 of 10
Report Number: 546883-S
Test Lab Sample ID QASource Units Result 1 Acceptance
LimitsPass
LimitsQualifying
Code
Perfluorobutanesulfonic acid(PFBS) S17-My22163 NCP % 109 50-150 Pass
Perfluoropentanesulfonic acid(PFPeS) S17-My22163 NCP % 108 50-150 Pass
Perfluorohexanesulfonic acid(PFHxS) S17-My22163 NCP % 108 50-150 Pass
Perfluoroheptanesulfonic acid(PFHpS) S17-My22163 NCP % 105 50-150 Pass
Perfluorooctanesulfonic acid(PFOS) S17-My22163 NCP % 31 50-150 Fail Q08
Perfluorodecanesulfonic acid(PFDS) S17-My22163 NCP % 91 50-150 Pass
Spike - % Recovery
n:2 Fluorotelomer sulfonic acids Result 1
1H.1H.2H.2H-perfluorohexanesulfonic acid (4:2FTS) S17-My22163 NCP % 116 50-150 Pass
1H.1H.2H.2H-perfluorooctanesulfonic acid (6:2FTS) S17-My22163 NCP % 146 50-150 Pass
1H.1H.2H.2H-perfluorodecanesulfonic acid (8:2FTS) S17-My22163 NCP % 109 50-150 Pass
1H.1H.2H.2H-perfluorododecanesulfonic acid(10:2 FTS) S17-My22163 NCP % 127 50-150 Pass
Test Lab Sample ID QASource Units Result 1 Acceptance
LimitsPass
LimitsQualifying
Code
Duplicate
Perfluoroalkyl carboxylic acids (PFCAs) Result 1 Result 2 RPD
Perfluorobutanoic acid (PFBA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluoropentanoic acid (PFPeA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorohexanoic acid (PFHxA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluoroheptanoic acid (PFHpA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorooctanoic acid (PFOA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorononanoic acid (PFNA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorodecanoic acid (PFDA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluoroundecanoic acid (PFUnA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorododecanoic acid (PFDoA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorotridecanoic acid (PFTrDA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorotetradecanoic acid(PFTeDA) B17-My24576 NCP ug/kg < 50 < 50 <1 30% Pass
Duplicate
Perfluoroalkane sulfonamides (PFASAs) Result 1 Result 2 RPD
Perfluorooctane sulfonamide(FOSA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
N-methylperfluoro-1-octanesulfonamide (N-MeFOSA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
N-ethylperfluoro-1-octanesulfonamide (N-EtFOSA) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
2-(N-methylperfluoro-1-octanesulfonamido)-ethanol (N-MeFOSE) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
2-(N-ethylperfluoro-1-octanesulfonamido)-ethanol (N-EtFOSE) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
N-ethyl-perfluorooctanesulfonamidoaceticacid (N-EtFOSAA) B17-My24576 NCP ug/kg < 10 < 10 <1 30% Pass
N-methyl-perfluorooctanesulfonamidoaceticacid (N-MeFOSAA) B17-My24576 NCP ug/kg < 10 < 10 <1 30% Pass
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 8 of 10
Report Number: 546883-S
Duplicate
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs) Result 1 Result 2 RPD
Perfluorobutanesulfonic acid(PFBS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluoropentanesulfonic acid(PFPeS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorohexanesulfonic acid(PFHxS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluoroheptanesulfonic acid(PFHpS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorooctanesulfonic acid(PFOS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Perfluorodecanesulfonic acid(PFDS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Duplicate
n:2 Fluorotelomer sulfonic acids Result 1 Result 2 RPD
1H.1H.2H.2H-perfluorohexanesulfonic acid (4:2FTS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
1H.1H.2H.2H-perfluorooctanesulfonic acid (6:2FTS) B17-My24576 NCP ug/kg < 10 < 10 <1 30% Pass
1H.1H.2H.2H-perfluorodecanesulfonic acid (8:2FTS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
1H.1H.2H.2H-perfluorododecanesulfonic acid(10:2 FTS) B17-My24576 NCP ug/kg < 5 < 5 <1 30% Pass
Duplicate
Result 1 Result 2 RPD
% Moisture M17-My13514 NCP % 15 14 7.0 30% Pass
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 9 of 10
Report Number: 546883-S
Comments
Sample IntegrityCustody Seals Intact (if used) N/A
Attempt to Chill was evident Yes
Sample correctly preserved Yes
Appropriate sample containers have been used Yes
Sample containers for volatile analysis received with minimal headspace Yes
Samples received within HoldingTime Yes
Some samples have been subcontracted No
Qualifier Codes/Comments
Code Description
N11
Isotope dilution is used for calibration of each native compound for which an exact labelled analogue is available (Isotope Dilution Quantitation). The isotopically labelledanalogues allow identification and recovery correction of the concentration of the associated native PFAS compounds. Where the native PFAS compound does not have labelledanalogue then the quantification is made using the Extracted Internal Standard Analyte with the closest retention time to the analyte and no recovery correction has been made(Internal Standard Quantitation).
Q08The matrix spike recovery is outside of the recommended acceptance criteria. An acceptable recovery was obtained for the laboratory control sample indicating a sample matrixinterference
Authorised By
Ryan Gilbert Analytical Services Manager
Bryan Wilson Senior Analyst-Metal (QLD)
Jonathon Angell Senior Analyst-Inorganic (QLD)
Jonathon Angell Senior Analyst-Organic (QLD)
Glenn Jackson
National Operations Manager
- Indicates Not Requested
* Indicates NATA accreditation does not cover the performance of this service
Measurement uncertainty of test data is available on request or please click here.Eurofins | mgt shall not be liable for loss, cost, damages or expenses incurred by the client, or any other person or company, resulting from the use of any information or interpretation given in this report. In no case shall Eurofins | mgt be liable for consequential damages including, but notlimited to, lost profits, damages for failure to meet deadlines and lost production arising from this report. This document shall not be reproduced except in full and relates only to the items tested. Unless indicated otherwise, the tests were performed on the samples as received.
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 10 of 10
Report Number: 546883-S
Certificate of Analysis
Golder Associates Pty Ltd
147 Coronation Dve
Milton
QLD 4064
Attention: Bianca Vanzati
Report 546883-W
Project name
Project ID 1669283
Received Date May 19, 2017
Client Sample ID 1218_QC210_170515
Sample Matrix Water
Eurofins | mgt Sample No. B17-My19669
Date Sampled May 15, 2017
Test/Reference LOR Unit
Perfluoroalkyl carboxylic acids (PFCAs)
Perfluorobutanoic acid (PFBA) 0.05 ug/L < 0.05
Perfluoropentanoic acid (PFPeA) 0.01 ug/L < 0.01
Perfluorohexanoic acid (PFHxA) 0.01 ug/L < 0.01
Perfluoroheptanoic acid (PFHpA) 0.01 ug/L < 0.01
Perfluorooctanoic acid (PFOA) 0.01 ug/L < 0.01
Perfluorononanoic acid (PFNA) 0.01 ug/L < 0.01
Perfluorodecanoic acid (PFDA) 0.01 ug/L < 0.01
Perfluoroundecanoic acid (PFUnA) 0.01 ug/L < 0.01
Perfluorododecanoic acid (PFDoA) 0.01 ug/L < 0.01
Perfluorotridecanoic acid (PFTrDA) 0.01 ug/L < 0.01
Perfluorotetradecanoic acid (PFTeDA) 0.01 ug/L < 0.01
13C4-PFBA (surr.) 1 % 90
13C5-PFPeA (surr.) 1 % 112
13C5-PFHxA (surr.) 1 % 146
13C4-PFHpA (surr.) 1 % 146
13C8-PFOA (surr.) 1 % 130
13C5-PFNA (surr.) 1 % 140
13C6-PFDA (surr.) 1 % 98
13C2-PFUnDA (surr.) 1 % 87
13C2-PFDoDA (surr.) 1 % 82
13C2-PFTeDA (surr.) 1 % 48
Perfluoroalkane sulfonamides (PFASAs)
Perfluorooctane sulfonamide (FOSA) 0.05 ug/L < 0.05
N-methylperfluoro-1-octane sulfonamide (N-MeFOSA) 0.05 ug/L < 0.05
N-ethylperfluoro-1-octane sulfonamide (N-EtFOSA) 0.05 ug/L < 0.05
2-(N-methylperfluoro-1-octane sulfonamido)-ethanol(N-MeFOSE) 0.05 ug/L < 0.05
2-(N-ethylperfluoro-1-octane sulfonamido)-ethanol (N-EtFOSE) 0.05 ug/L < 0.05
N-ethyl-perfluorooctanesulfonamidoacetic acid (N-EtFOSAA) 0.05 ug/L < 0.05
N-methyl-perfluorooctanesulfonamidoacetic acid (N-MeFOSAA) 0.05 ug/L < 0.05
13C8-FOSA (surr.) 1 % 92
D3-N-MeFOSA (surr.) 1 % 60
D5-N-EtFOSA (surr.) 1 % 56
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 1 of 7
Report Number: 546883-W
NATA AccreditedAccreditation Number 1261Site Number 20794
Accredited for compliance with ISO/IEC 17025 – TestingThe results of the tests, calibrations and/ormeasurements included in this document are traceableto Australian/national standards.
Client Sample ID 1218_QC210_170515
Sample Matrix Water
Eurofins | mgt Sample No. B17-My19669
Date Sampled May 15, 2017
Test/Reference LOR Unit
Perfluoroalkane sulfonamides (PFASAs)
D7-N-MeFOSE (surr.) 1 % 59
D9-N-EtFOSE (surr.) 1 % 67
D5-N-EtFOSAA (surr.) 1 % 87
D3-N-MeFOSAA (surr.) 1 % 98
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs)
Perfluorobutanesulfonic acid (PFBS) 0.01 ug/L < 0.01
Perfluoropentanesulfonic acid (PFPeS) 0.01 ug/L < 0.01
Perfluorohexanesulfonic acid (PFHxS) 0.01 ug/L < 0.01
Perfluoroheptanesulfonic acid (PFHpS) 0.01 ug/L < 0.01
Perfluorooctanesulfonic acid (PFOS)N11 0.01 ug/L N090.01
Perfluorodecanesulfonic acid (PFDS) 0.01 ug/L < 0.01
13C3-PFBS (surr.) 1 % 127
18O2-PFHxS (surr.) 1 % 129
13C8-PFOS (surr.) 1 % 123
n:2 Fluorotelomer sulfonic acids
1H.1H.2H.2H-perfluorohexanesulfonic acid (4:2 FTS) 0.01 ug/L < 0.01
1H.1H.2H.2H-perfluorooctanesulfonic acid (6:2 FTS) 0.05 ug/L < 0.05
1H.1H.2H.2H-perfluorodecanesulfonic acid (8:2 FTS) 0.01 ug/L < 0.01
1H.1H.2H.2H-perfluorododecanesulfonic acid (10:2FTS) 0.01 ug/L < 0.01
13C2-4:2 FTS (surr.) 1 % 198
13C2-6:2 FTS (surr.) 1 % 144
13C2-8:2 FTS (surr.) 1 % 106
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 2 of 7
Report Number: 546883-W
Sample HistoryWhere samples are submitted/analysed over several days, the last date of extraction and analysis is reported.A recent review of our LIMS has resulted in the correction or clarification of some method identifications. Due to this, some of the method reference information on reports has changed. However,no substantive change has been made to our laboratory methods, and as such there is no change in the validity of current or previous results (regarding both quality and NATA accreditation).
If the date and time of sampling are not provided, the Laboratory will not be responsible for compromised results should testing be performed outside the recommended holding time.
Description Testing Site Extracted Holding Time
Per- and Polyfluorinated Alkyl Substances (PFASs)
Perfluoroalkyl carboxylic acids (PFCAs) Brisbane May 19, 2017 14 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
Perfluoroalkane sulfonamides (PFASAs) Brisbane May 19, 2017 14 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
Perfluoroalkane sulfonic acids & Perfluoroalkane sulfonates (PFSAs) Brisbane May 19, 2017 14 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
n:2 Fluorotelomer sulfonic acids Brisbane May 19, 2017 14 Day
- Method: LTM-ORG-2100 Per- and Polyfluorinated Alkyl Substances by LC-MS/MS
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 3 of 7
Report Number: 546883-W
.Company Name: Golder Associates Pty Ltd (Qld) Order No.: Received: May 19, 2017 2:45 PMAddress: 147 Coronation Dve Report #: 546883 Due: May 26, 2017
Milton Phone: (07) 3721 5400 Priority: 5 DayQLD 4064 Fax: (07) 3721 5401 Contact Name: Fran Mitchell
Project Name:Project ID: 1669283
Eurofins | mgt Analytical Services Manager : Ryan Gilbert
Sample Detail
Moisture S
et
Per- and P
olyfluorinated Alkyl S
ubstances(P
FA
Ss)
Melbourne Laboratory - NATA Site # 1254 & 14271
Sydney Laboratory - NATA Site # 18217
Brisbane Laboratory - NATA Site # 20794 X X
Perth Laboratory - NATA Site # 18217
External Laboratory
No Sample ID Sample Date SamplingTime
Matrix LAB ID
1 1218_QC208_170513
May 13, 2017 Soil B17-My19667 X X
2 1218_QC207_170512
May 12, 2017 Soil B17-My19668 X X
3 1218_QC210_170515
May 15, 2017 Water B17-My19669 X
Test Counts 2 3
ABN– 50 005 085 521e.mail : [email protected] : www.eurofins.com.au
MelbourneMelbourneMelbourneMelbourne2-5 Kingston Town CloseOakleigh VIC 3166Phone : +61 3 8564 5000NATA # 1261Site # 1254 & 14271
SydneySydneySydneySydneyUnit F3, Building F16 Mars RoadLane Cove West NSW 2066Phone : +61 2 9900 8400NATA # 1261 Site # 18217
BrisbaneBrisbaneBrisbaneBrisbane1/21 Smallwood PlaceMurarrie QLD 4172Phone : +61 7 3902 4600NATA # 1261 Site # 20794
PerthPerthPerthPerth2/91 Leach HighwayKewdale WA 6105Phone : +61 8 9251 9600NATA # 1261Site # 18217
Date Reported:Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 4 of 7
Report Number: 546883-W
Internal Quality Control Review and Glossary
General
Holding Times
Units
Terms
QC - Acceptance Criteria
QC Data General Comments
1. Laboratory QC results for Method Blanks, Duplicates, Matrix Spikes, and Laboratory Control Samples are included in this QC report where applicable. Additional QC data may be available on
request.
2. All soil results are reported on a dry basis, unless otherwise stated.
3. All biota results are reported on a wet weight basis on the edible portion, unless otherwise stated.
4. Actual LORs are matrix dependant. Quoted LORs may be raised where sample extracts are diluted due to interferences.
5. Results are uncorrected for matrix spikes or surrogate recoveries.
6. SVOC analysis on waters are performed on homogenised, unfiltered samples, unless noted otherwise.
7. Samples were analysed on an 'as received' basis.
8. This report replaces any interim results previously issued.
Please refer to 'Sample Preservation and Container Guide' for holding times (QS3001).
For samples received on the last day of holding time, notification of testing requirements should have been received at least 6 hours prior to sample receipt deadlines as stated on the Sample
Receipt Advice.
If the Laboratory did not receive the information in the required timeframe, and regardless of any other integrity issues, suitably qualified results may still be reported.
Holding times apply from the date of sampling, therefore compliance to these may be outside the laboratory's control.
**NOTE: pH duplicates are reported as a range NOT as RPD
mg/kg: milligrams per kilogram mg/L: milligrams per litre
ug/L: micrograms per litre ppm: Parts per million
ppb: Parts per billion %: Percentage
org/100mL: Organisms per 100 millilitres NTU: Nephelometric Turbidity Units
MPN/100mL: Most Probable Number of organisms per 100 millilitres
Dry Where a moisture has been determined on a solid sample the result is expressed on a dry basis.
LOR Limit of Reporting.
SPIKE Addition of the analyte to the sample and reported as percentage recovery.
RPD Relative Percent Difference between two Duplicate pieces of analysis.
LCS Laboratory Control Sample - reported as percent recovery.
CRM Certified Reference Material - reported as percent recovery.
Method Blank In the case of solid samples these are performed on laboratory certified clean sands.
In the case of water samples these are performed on de-ionised water.
Surr - Surrogate The addition of a like compound to the analyte target and reported as percentage recovery.
Duplicate A second piece of analysis from the same sample and reported in the same units as the result to show comparison.
Batch Duplicate A second piece of analysis from a sample outside of the clients batch of samples but run within the laboratory batch of analysis.
Batch SPIKE Spike recovery reported on a sample from outside of the clients batch of samples but run within the laboratory batch of analysis.
USEPA United States Environmental Protection Agency
APHA American Public Health Association
TCLP Toxicity Characteristic Leaching Procedure
COC Chain of Custody
SRA Sample Receipt Advice
CP Client Parent - QC was performed on samples pertaining to this report
NCP Non-Client Parent - QC performed on samples not pertaining to this report, QC is representative of the sequence or batch that client samples were analysed within.
TEQ Toxic Equivalency Quotient
RPD Duplicates: Global RPD Duplicates Acceptance Criteria is 30% however the following acceptance guidelines are equally applicable:
Results <10 times the LOR : No Limit
Results between 10-20 times the LOR : RPD must lie between 0-50%
Results >20 times the LOR : RPD must lie between 0-30%
Surrogate Recoveries: Recoveries must lie between 50-150%-Phenols & PFASs 20-130%
1. Where a result is reported as a less than (<), higher than the nominated LOR, this is due to either matrix interference, extract dilution required due to interferences or contaminant levels within
the sample, high moisture content or insufficient sample provided.
2. Duplicate data shown within this report that states the word "BATCH" is a Batch Duplicate from outside of your sample batch, but within the laboratory sample batch at a 1:10 ratio. The Parent
and Duplicate data shown is not data from your samples.
3. Organochlorine Pesticide analysis - where reporting LCS data, Toxaphene & Chlordane are not added to the LCS.
4. Organochlorine Pesticide analysis - where reporting Spike data, Toxaphene is not added to the Spike.
5. Total Recoverable Hydrocarbons - where reporting Spike & LCS data, a single spike of commercial Hydrocarbon products in the range of C12-C30 is added and it's Total Recovery is reported
in the C10-C14 cell of the Report.
6. pH and Free Chlorine analysed in the laboratory - Analysis on this test must begin within 30 minutes of sampling.Therefore laboratory analysis is unlikely to be completed within holding time.
Analysis will begin as soon as possible after sample receipt.
7. Recovery Data (Spikes & Surrogates) - where chromatographic interference does not allow the determination of Recovery the term "INT" appears against that analyte.
8. Polychlorinated Biphenyls are spiked only using Aroclor 1260 in Matrix Spikes and LCS.
9. For Matrix Spikes and LCS results a dash " -" in the report means that the specific analyte was not added to the QC sample.
10. Duplicate RPDs are calculated from raw analytical data thus it is possible to have two sets of data.
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 5 of 7
Report Number: 546883-W
Quality Control Results
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 6 of 7
Report Number: 546883-W
Comments
Sample IntegrityCustody Seals Intact (if used) N/A
Attempt to Chill was evident Yes
Sample correctly preserved Yes
Appropriate sample containers have been used Yes
Sample containers for volatile analysis received with minimal headspace Yes
Samples received within HoldingTime Yes
Some samples have been subcontracted No
Qualifier Codes/Comments
Code DescriptionN09 Quantification of linear and branched isomers has been conducted as a single total response using the relative response factor for the corresponding linear/branched standard.
N11
Isotope dilution is used for calibration of each native compound for which an exact labelled analogue is available (Isotope Dilution Quantitation). The isotopically labelledanalogues allow identification and recovery correction of the concentration of the associated native PFAS compounds. Where the native PFAS compound does not have labelledanalogue then the quantification is made using the Extracted Internal Standard Analyte with the closest retention time to the analyte and no recovery correction has been made(Internal Standard Quantitation).
Authorised By
Ryan Gilbert Analytical Services Manager
Jonathon Angell Senior Analyst-Organic (QLD)
Glenn Jackson
National Operations Manager
- Indicates Not Requested
* Indicates NATA accreditation does not cover the performance of this service
Measurement uncertainty of test data is available on request or please click here.Eurofins | mgt shall not be liable for loss, cost, damages or expenses incurred by the client, or any other person or company, resulting from the use of any information or interpretation given in this report. In no case shall Eurofins | mgt be liable for consequential damages including, but notlimited to, lost profits, damages for failure to meet deadlines and lost production arising from this report. This document shall not be reproduced except in full and relates only to the items tested. Unless indicated otherwise, the tests were performed on the samples as received.
Date Reported: Jun 01, 2017
Eurofins | mgt 1/21 Smallwood Place, Murarrie, QLD, Australia, 4172
ABN : 50 005 085 521 Telephone: +61 7 3902 4600
Page 7 of 7
Report Number: 546883-W
ABN – 50 005 085 521 e.mail : [email protected] web : www.eurofins.com.au
MelbourneMelbourneMelbourneMelbourne3-5 Kingston Town CloseOakleigh Vic 3166Phone : +61 3 8564 5000NATA # 1261Site # 1254 & 14271
SydneySydneySydneySydneyUnit F3, Building F16 Mars RoadLane Cove West NSW 2066Phone : +61 2 9900 8400NATA # 1261 Site # 18217
BrisbaneBrisbaneBrisbaneBrisbane1/21 Smallwood PlaceMurarrie QLD 4172Phone : +61 7 3902 4600NATA # 1261 Site # 20794
PerthPerthPerthPerth2/91 Leach HighwayKewdale WA 6105Phone : +61 8 9251 9600NATA # 1261 Site # 18217
Environmental LaboratoryAir AnalysisWater AnalysisSoil Contamination Analysis
NATA AccreditationStack Emission Sampling & AnalysisTrade Waste Sampling & AnalysisGroundwater Sampling & Analysis
38 Years of Environmental Analysis & Experience38 Years of Environmental Analysis & Experience38 Years of Environmental Analysis & Experience38 Years of Environmental Analysis & Experience
Sample Receipt AdviceSample Receipt AdviceSample Receipt AdviceSample Receipt Advice
Company name: Golder Associates Pty Ltd (Qld)Golder Associates Pty Ltd (Qld)Golder Associates Pty Ltd (Qld)Golder Associates Pty Ltd (Qld)
Contact name: Fran MitchellProject ID: 1669283COC number: Not providedTurn around time: 5 DayDate/Time received: May 19, 2017 2:45 PMEurofins | mgt reference: 546883546883546883546883
Sample informationSample informationSample informationSample information
☑ A detailed list of analytes logged into our LIMS, is included in the attached summary table.
☑ Sample Temperature of a random sample selected from the batch as recorded by Eurofins | mgtSample Receipt : 7.3 degrees Celsius.
☑ All samples have been received as described on the above COC.
☑ COC has been completed correctly.
☑ Attempt to chill was evident.
☑ Appropriately preserved sample containers have been used.
☑ All samples were received in good condition.
☑ Samples have been provided with adequate time to commence analysis in accordance with therelevant holding times.
☑ Appropriate sample containers have been used.
☑ Sample containers for volatile analysis received with zero headspace.
☒ Some samples have been subcontracted.
N/A Custody Seals intact (if used).
Contact notesContact notesContact notesContact notes
If you have any questions with respect to these samples please contact:
Ryan Gilbert on Phone : or by e.mail: [email protected]
Results will be delivered electronically via e.mail to Fran Mitchell - [email protected].
False
3 3.00True
Environmental
QUALITY CONTROL REPORTWork Order : EB1709386 Page : 1 of 11
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL :Contact Matt Frost
:Address 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
Address : 2 Byth Street Stafford QLD Australia 4053
::Telephone +61 07 3721 5400 +61-7-3243 7222:Telephone
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017
:Order number 1669283 Date Analysis Commenced : 12-May-2017
:C-O-C number ---- Issue Date : 16-May-2017
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
No. of samples received 14:
No. of samples analysed 14:
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Quality Control Report contains the following information:
l Laboratory Duplicate (DUP) Report; Relative Percentage Difference (RPD) and Acceptance Limits
l Method Blank (MB) and Laboratory Control Spike (LCS) Report ; Recovery and Acceptance Limits
l Matrix Spike (MS) Report; Recovery and Acceptance Limits
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
Edwandy Fadjar Organic Coordinator Sydney Inorganics, Smithfield, NSW
Lana Nguyen Senior LCMS Chemist Sydney Organics, Smithfield, NSW
R I G H T S O L U T I O N S | R I G H T P A R T N E R
2 of 11:Page
Work Order :
:Client
EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis. Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
Anonymous = Refers to samples which are not specifically part of this work order but formed part of the QC process lot
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
RPD = Relative Percentage Difference
# = Indicates failed QC
Key :
Laboratory Duplicate (DUP) Report
The quality control term Laboratory Duplicate refers to a randomly selected intralaboratory split. Laboratory duplicates provide information regarding method precision and sample heterogeneity. The permitted ranges
for the Relative Percent Deviation (RPD) of Laboratory Duplicates are specified in ALS Method QWI -EN/38 and are dependent on the magnitude of results in comparison to the level of reporting: Result < 10 times LOR:
No Limit; Result between 10 and 20 times LOR: 0% - 50%; Result > 20 times LOR: 0% - 20%.
Sub-Matrix: SOIL Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EA055: Moisture Content (QC Lot: 883736)
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 10.3 10.6 2.83 0% - 50%Anonymous EB1709261-001
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 22.7 24.2 6.50 0% - 20%1218_SD006_0.0_170505 EB1709386-006
EA055: Moisture Content (QC Lot: 883737)
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 22.1 23.8 7.32 0% - 20%Anonymous EP1704710-003
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 19.6 21.2 7.60 0% - 20%Anonymous ES1710536-005
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 883909)
EP231X: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_SD001_0.0_170504 EB1709386-001
EP231X: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.0002 mg/kg 0.0019 0.0018 7.28 No Limit
EP231X: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.0002 mg/kg 0.0004 0.0004 0.00 No Limit
EP231X: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_QC102_170504 EB1709386-011
EP231X: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.0002 mg/kg 0.0010 0.0010 0.00 No Limit
EP231X: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 883909)
EP231X: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_SD001_0.0_170504 EB1709386-001
EP231X: Perfluorohexanoic acid (PFHxA) 307-24-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorooctanoic acid (PFOA) 335-67-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorononanoic acid (PFNA) 375-95-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
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:Client
EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: SOIL Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 883909) - continued
EP231X: Perfluorodecanoic acid (PFDA) 335-76-2 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_SD001_0.0_170504 EB1709386-001
EP231X: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: Perfluorobutanoic acid (PFBA) 375-22-4 0.001 mg/kg <0.001 <0.001 0.00 No Limit
EP231X: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_QC102_170504 EB1709386-011
EP231X: Perfluorohexanoic acid (PFHxA) 307-24-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorooctanoic acid (PFOA) 335-67-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorononanoic acid (PFNA) 375-95-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorodecanoic acid (PFDA) 335-76-2 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: Perfluorobutanoic acid (PFBA) 375-22-4 0.001 mg/kg <0.001 <0.001 0.00 No Limit
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 883909)
EP231X: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_SD001_0.0_170504 EB1709386-001
EP231X: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_QC102_170504 EB1709386-011
EP231X: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
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GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: SOIL Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 883909) - continued
EP231X: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit1218_QC102_170504 EB1709386-011
EP231X: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QC Lot: 883909)
EP231X: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit1218_SD001_0.0_170504 EB1709386-001
EP231X: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 10:2 Fluorotelomer sulfonic acid (10:2
FTS)
120226-60-0 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit1218_QC102_170504 EB1709386-011
EP231X: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 10:2 Fluorotelomer sulfonic acid (10:2
FTS)
120226-60-0 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 887692)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_QC301_170504 EB1709386-012
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L 0.023 0.020 12.6 0% - 50%Anonymous ES1711269-001
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L 0.007 0.004 49.6 No Limit
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L 0.230 0.215 7.10 0% - 20%
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EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 887692) - continued
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L 0.003 0.004 0.00 No LimitAnonymous ES1711269-001
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L 0.083 0.076 8.77 0% - 20%
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 887692)
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_QC301_170504 EB1709386-012
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L 0.034 0.032 6.39 0% - 50%Anonymous ES1711269-001
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L 0.143 0.124 14.4 0% - 20%
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L 0.027 0.022 21.1 0% - 50%
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L 0.072 0.078 7.34 0% - 20%
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L 0.004 0.003 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 887692)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_QC301_170504 EB1709386-012
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No Limit
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EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 887692) - continued
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit1218_QC301_170504 EB1709386-012
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No LimitAnonymous ES1711269-001
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L 0.013 0.013 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L 0.024 0.021 13.9 0% - 50%
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QC Lot: 887692)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No Limit1218_QC301_170504 EB1709386-012
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No LimitAnonymous ES1711269-001
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
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1669283 Phase: 9202:Project
Method Blank (MB) and Laboratory Control Spike (LCS) Report
The quality control term Method / Laboratory Blank refers to an analyte free matrix to which all reagents are added in the same volumes or proportions as used in standard sample preparation. The purpose of this QC
parameter is to monitor potential laboratory contamination. The quality control term Laboratory Control Spike (LCS) refers to a certified reference material, or a known interference free matrix spiked with target
analytes. The purpose of this QC parameter is to monitor method precision and accuracy independent of sample matrix. Dynamic Recovery Limits are based on statistical evaluation of processed LCS.
Sub-Matrix: SOIL Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 883909)
EP231X: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.0002 mg/kg <0.0002 87.40.00125 mg/kg 12157
EP231X: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.0002 mg/kg <0.0002 87.60.00125 mg/kg 12555
EP231X: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.0002 mg/kg <0.0002 87.80.00125 mg/kg 12652
EP231X: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.0002 mg/kg <0.0002 83.30.00125 mg/kg 12354
EP231X: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.0002 mg/kg <0.0002 75.10.00125 mg/kg 12755
EP231X: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.0002 mg/kg <0.0002 82.20.00125 mg/kg 12554
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 883909)
EP231X: Perfluorobutanoic acid (PFBA) 375-22-4 0.001 mg/kg <0.001 89.10.00625 mg/kg 12852
EP231X: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.0002 mg/kg <0.0002 1010.00125 mg/kg 12954
EP231X: Perfluorohexanoic acid (PFHxA) 307-24-4 0.0002 mg/kg <0.0002 89.10.00125 mg/kg 12758
EP231X: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.0002 mg/kg <0.0002 1060.00125 mg/kg 12857
EP231X: Perfluorooctanoic acid (PFOA) 335-67-1 0.0002 mg/kg <0.0002 80.30.00125 mg/kg 13460
EP231X: Perfluorononanoic acid (PFNA) 375-95-1 0.0002 mg/kg <0.0002 98.90.00125 mg/kg 13063
EP231X: Perfluorodecanoic acid (PFDA) 335-76-2 0.0002 mg/kg <0.0002 86.50.00125 mg/kg 13055
EP231X: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.0002 mg/kg <0.0002 88.90.00125 mg/kg 13062
EP231X: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.0002 mg/kg <0.0002 94.90.00125 mg/kg 13453
EP231X: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.0002 mg/kg <0.0002 94.50.00125 mg/kg 12949
EP231X: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.0005 mg/kg <0.0005 92.20.00312 mg/kg 12959
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883909)
EP231X: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.0002 mg/kg <0.0002 94.30.00125 mg/kg 13252
EP231X: N-Methyl perfluorooctane sulfonamide (MeFOSA) 31506-32-8 0.0005 mg/kg <0.0005 96.10.00312 mg/kg 12665
EP231X: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 4151-50-2 0.0005 mg/kg <0.0005 90.80.00312 mg/kg 12664
EP231X: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
2448-09-7 0.0005 mg/kg <0.0005 99.50.00312 mg/kg 12463
EP231X: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
1691-99-2 0.0005 mg/kg <0.0005 1040.00312 mg/kg 12558
EP231X: N-Methyl perfluorooctane sulfonamidoacetic acid
(MeFOSAA)
2355-31-9 0.0002 mg/kg <0.0002 81.40.00125 mg/kg 13061
EP231X: N-Ethyl perfluorooctane sulfonamidoacetic acid
(EtFOSAA)
2991-50-6 0.0002 mg/kg <0.0002 87.20.00125 mg/kg 13055
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883909)
EP231X: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 757124-72-4 0.0005 mg/kg <0.0005 92.00.00125 mg/kg 13054
EP231X: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 27619-97-2 0.0005 mg/kg <0.0005 89.90.00125 mg/kg 13061
EP231X: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 39108-34-4 0.0005 mg/kg <0.0005 91.50.00125 mg/kg 13062
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Sub-Matrix: SOIL Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883909) - continued
EP231X: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 120226-60-0 0.0005 mg/kg <0.0005 87.00.00125 mg/kg 13060
Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 887692)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 1030.05 µg/L 13060
EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.002 µg/L <0.002 93.60.05 µg/L 13060
EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.002 µg/L <0.002 1100.05 µg/L 13060
EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.002 µg/L <0.002 1080.05 µg/L 13060
EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.002 µg/L <0.002 91.00.05 µg/L 13060
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 887692)
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 1250.25 µg/L 13060
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 89.80.05 µg/L 13060
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 93.00.05 µg/L 13060
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 75.80.05 µg/L 13060
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 88.00.05 µg/L 13060
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 83.40.05 µg/L 13060
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 87.80.05 µg/L 13060
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 94.80.05 µg/L 13060
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 96.80.05 µg/L 13060
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 75.60.05 µg/L 13060
EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.005 µg/L <0.005 86.30.125 µg/L 13060
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 887692)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 96.20.05 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.005 µg/L <0.005 95.80.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 4151-50-2 0.005 µg/L <0.005 94.50.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
2448-09-7 0.005 µg/L <0.005 96.40.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
1691-99-2 0.005 µg/L <0.005 96.80.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoacetic
acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 62.00.05 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 81.80.05 µg/L 13060
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 887692)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 757124-72-4 0.005 µg/L <0.005 75.80.05 µg/L 13060
9 of 11:Page
Work Order :
:Client
EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 887692) - continued
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 27619-97-2 0.005 µg/L <0.005 1120.05 µg/L 13060
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 39108-34-4 0.005 µg/L <0.005 70.60.05 µg/L 13060
EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 120226-60-0 0.005 µg/L <0.005 97.40.05 µg/L 13060
Matrix Spike (MS) ReportThe quality control term Matrix Spike (MS) refers to an intralaboratory split sample spiked with a representative set of target analytes. The purpose of this QC parameter is to monitor potential matrix effects on
analyte recoveries. Static Recovery Limits as per laboratory Data Quality Objectives (DQOs). Ideal recovery ranges stated may be waived in the event of sample matrix interference.
Sub-Matrix: SOIL Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 883909)
1218_SD001_0.0_170504 EB1709386-001 375-73-5EP231X: Perfluorobutane sulfonic acid (PFBS) 81.80.00125 mg/kg 13050
2706-91-4EP231X: Perfluoropentane sulfonic acid (PFPeS) 72.20.00125 mg/kg 13050
355-46-4EP231X: Perfluorohexane sulfonic acid (PFHxS) 56.00.00125 mg/kg 13050
375-92-8EP231X: Perfluoroheptane sulfonic acid (PFHpS) 64.40.00125 mg/kg 13050
1763-23-1EP231X: Perfluorooctane sulfonic acid (PFOS) 79.80.00125 mg/kg 13050
335-77-3EP231X: Perfluorodecane sulfonic acid (PFDS) 69.80.00125 mg/kg 13050
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 883909)
1218_SD001_0.0_170504 EB1709386-001 375-22-4EP231X: Perfluorobutanoic acid (PFBA) 91.50.00625 mg/kg 13030
2706-90-3EP231X: Perfluoropentanoic acid (PFPeA) 1100.00125 mg/kg 13050
307-24-4EP231X: Perfluorohexanoic acid (PFHxA) 77.70.00125 mg/kg 13050
375-85-9EP231X: Perfluoroheptanoic acid (PFHpA) 65.40.00125 mg/kg 13050
335-67-1EP231X: Perfluorooctanoic acid (PFOA) 70.10.00125 mg/kg 13050
375-95-1EP231X: Perfluorononanoic acid (PFNA) 80.60.00125 mg/kg 13050
335-76-2EP231X: Perfluorodecanoic acid (PFDA) 59.90.00125 mg/kg 13050
2058-94-8EP231X: Perfluoroundecanoic acid (PFUnDA) 75.00.00125 mg/kg 13050
307-55-1EP231X: Perfluorododecanoic acid (PFDoDA) 61.20.00125 mg/kg 13050
72629-94-8EP231X: Perfluorotridecanoic acid (PFTrDA) 59.00.00125 mg/kg 13030
376-06-7EP231X: Perfluorotetradecanoic acid (PFTeDA) 51.30.00312 mg/kg 13030
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883909)
1218_SD001_0.0_170504 EB1709386-001 754-91-6EP231X: Perfluorooctane sulfonamide (FOSA) 55.90.00125 mg/kg 13050
31506-32-8EP231X: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
66.20.00312 mg/kg 13030
4151-50-2EP231X: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 73.70.00312 mg/kg 13030
2448-09-7EP231X: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
60.20.00312 mg/kg 13030
10 of 11:Page
Work Order :
:Client
EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: SOIL Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883909) - continued
1218_SD001_0.0_170504 EB1709386-001 1691-99-2EP231X: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
67.40.00312 mg/kg 13030
2355-31-9EP231X: N-Methyl perfluorooctane sulfonamidoacetic
acid (MeFOSAA)
83.50.00125 mg/kg 13030
2991-50-6EP231X: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
53.20.00125 mg/kg 13030
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883909)
1218_SD001_0.0_170504 EB1709386-001 757124-72-4EP231X: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 1130.00125 mg/kg 13050
27619-97-2EP231X: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 94.50.00125 mg/kg 13050
39108-34-4EP231X: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 78.90.00125 mg/kg 13050
120226-60-0EP231X: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 68.40.00125 mg/kg 13050
Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 887692)
Anonymous EM1706014-001 375-73-5EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 1180.05 µg/L 13050
2706-91-4EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 77.80.05 µg/L 13050
355-46-4EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 1040.05 µg/L 13050
375-92-8EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 80.80.05 µg/L 13050
1763-23-1EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 98.60.05 µg/L 13050
335-77-3EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 1040.05 µg/L 13050
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 887692)
Anonymous EM1706014-001 375-22-4EP231X-LL: Perfluorobutanoic acid (PFBA) 54.80.25 µg/L 13030
2706-90-3EP231X-LL: Perfluoropentanoic acid (PFPeA) 68.40.05 µg/L 13050
307-24-4EP231X-LL: Perfluorohexanoic acid (PFHxA) 94.20.05 µg/L 13050
375-85-9EP231X-LL: Perfluoroheptanoic acid (PFHpA) 74.20.05 µg/L 13050
335-67-1EP231X-LL: Perfluorooctanoic acid (PFOA) 84.60.05 µg/L 13050
375-95-1EP231X-LL: Perfluorononanoic acid (PFNA) 65.80.05 µg/L 13050
335-76-2EP231X-LL: Perfluorodecanoic acid (PFDA) 70.20.05 µg/L 13050
2058-94-8EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 70.20.05 µg/L 13050
307-55-1EP231X-LL: Perfluorododecanoic acid (PFDoDA) 67.20.05 µg/L 13050
72629-94-8EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 83.40.05 µg/L 13030
376-06-7EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 68.10.125 µg/L 13030
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 887692)
Anonymous EM1706014-001 754-91-6EP231X-LL: Perfluorooctane sulfonamide (FOSA) 1060.05 µg/L 13050
31506-32-8EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
1020.125 µg/L 13030
11 of 11:Page
Work Order :
:Client
EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 887692) - continued
Anonymous EM1706014-001 4151-50-2EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
71.80.125 µg/L 13030
2448-09-7EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
80.20.125 µg/L 13030
1691-99-2EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
69.30.125 µg/L 13030
2355-31-9EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
58.80.05 µg/L 13040
2991-50-6EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
73.20.05 µg/L 13040
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 887692)
Anonymous EM1706014-001 757124-72-4EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 70.00.05 µg/L 13050
27619-97-2EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 67.20.05 µg/L 13050
39108-34-4EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 70.40.05 µg/L 13050
120226-60-0EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 1080.05 µg/L 13050
Environmental
SAMPLE RECEIPT NOTIFICATION (SRN)Work Order : EB1709386
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia
4053
:: E-mailE-mail [email protected] [email protected]
:: TelephoneTelephone +61 07 3721 5400 +61-7-3243 7222
:: FacsimileFacsimile +61 07 3721 5401 +61-7-3243 7218
::Project 1669283 Phase: 9202 Page 1 of 3
:Order number 1669283 :Quote number ES2016GOLASS0005 (EN/002/16 v2)
:C-O-C number ---- :QC Level NEPM 2013 B3 & ALS QC Standard
Site : ----
Sampler : DARCY SIMPSON
DatesDate Samples Received : Issue Date : 09-May-201709-May-2017 09:00
Scheduled Reporting Date: 16-May-2017:Client Requested Due
Date
16-May-2017
Delivery DetailsMode of Delivery : :Carrier Intact.Security Seal
No. of coolers/boxes : :1 Temperature 4.5°C - Ice present
: : 14 / 14MEDIUM ESKYReceipt Detail No. of samples received / analysed
General Comments
This report contains the following information:l
- Sample Container(s)/Preservation Non-Compliances
- Summary of Sample(s) and Requested Analysis
- Proactive Holding Time Report
- Requested Deliverables
l Discounted Package Prices apply only when specific ALS Group Codes ('W', 'S', 'NT' suites) are referenced on COCs.
l Analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site No.
10911 (Micro site no. 14913).l Please direct any turn around / technical queries to the laboratory contact designated above.
l Sample Disposal - Aqueous (14 days), Solid (60 days) from date of completion of work order.
l Breaches in recommended extraction / analysis holding times (if any) are displayed overleaf in
the Proactive Holding Time Report table.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
:Client GOLDER ASSOCIATES
Work Order : EB1709386 Amendment 02 of 3:Page
09-May-2017:Issue Date
Sample Container(s)/Preservation Non-Compliances
All comparisons are made against pretreatment/preservation AS, APHA, USEPA standards.
l No sample container / preservation non-compliance exists.
Any sample identifications that cannot be displayed entirely in the analysis summary table will be listed below.
EB1709386-001 : [ 04-May-2017 ] : 1218_SD001_0.0_170504
EB1709386-002 : [ 04-May-2017 ] : 1218_SD002_0.0_170504
EB1709386-003 : [ 04-May-2017 ] : 1218_SD003_0.0_170504
EB1709386-004 : [ 04-May-2017 ] : 1218_SD004_0.0_170504
EB1709386-005 : [ 04-May-2017 ] : 1218_SD005_0.0_170504
EB1709386-006 : [ 05-May-2017 ] : 1218_SD006_0.0_170505
EB1709386-007 : [ 05-May-2017 ] : 1218_SD007_0.0_170505
EB1709386-008 : [ 05-May-2017 ] : 1218_SD008_0.0_170505
EB1709386-009 : [ 05-May-2017 ] : 1218_SD009_0.0_170505
EB1709386-010 : [ 05-May-2017 ] : 1218_SD010_0.0_170505
EB1709386-013 : [ 05-May-2017 ] : 1218_SD011_0.0_170505
EB1709386-014 : [ 05-May-2017 ] : 1218_SD012_0.0_170505
Summary of Sample(s) and Requested Analysis
Some items described below may be part of a laboratory
process necessary for the execution of client requested
tasks. Packages may contain additional analyses, such
as the determination of moisture content and preparation
tasks, that are included in the package.
If no sampling time is provided, the sampling time will
default 00:00 on the date of sampling. If no sampling date
is provided, the sampling date will be assumed by the
laboratory and displayed in brackets without a time
component
SO
IL -
EA
05
5-1
03
Mo
istu
re C
on
ten
t
SO
IL -
EP
23
1X
(so
lids)
PF
AS
- F
ull
Su
ite (
28
an
aly
tes)
EB1709386-001 [ 04-May-2017 ] 1218_SD001_0.0_170504 ü ü
EB1709386-002 [ 04-May-2017 ] 1218_SD002_0.0_170504 ü ü
EB1709386-003 [ 04-May-2017 ] 1218_SD003_0.0_170504 ü ü
EB1709386-004 [ 04-May-2017 ] 1218_SD004_0.0_170504 ü ü
EB1709386-005 [ 04-May-2017 ] 1218_SD005_0.0_170504 ü ü
EB1709386-006 [ 05-May-2017 ] 1218_SD006_0.0_170505 ü ü
EB1709386-007 [ 05-May-2017 ] 1218_SD007_0.0_170505 ü ü
EB1709386-008 [ 05-May-2017 ] 1218_SD008_0.0_170505 ü ü
EB1709386-009 [ 05-May-2017 ] 1218_SD009_0.0_170505 ü ü
EB1709386-010 [ 05-May-2017 ] 1218_SD010_0.0_170505 ü ü
EB1709386-011 [ 04-May-2017 ] 1218_QC102_170504 ü ü
EB1709386-013 [ 05-May-2017 ] 1218_SD011_0.0_170505 ü ü
EB1709386-014 [ 05-May-2017 ] 1218_SD012_0.0_170505 ü ü
Matrix: SOIL
Client sample IDLaboratory sample
ID
Client sampling
date / time
:Client GOLDER ASSOCIATES
Work Order : EB1709386 Amendment 03 of 3:Page
09-May-2017:Issue Date
WA
TE
R -
EP
23
1X
-LL
PF
AS
- F
ull
Suite
Low
Leve
l (28
ana
lyte
s)
EB1709386-012 [ 04-May-2017 ] 1218_QC301_170504 ü
Matrix: WATER
Client sample IDLaboratory sample
ID
Client sampling
date / time
Proactive Holding Time Report
Sample(s) have been received within the recommended holding times for the requested analysis.
Requested Deliverables
ACCOUNTS PAYABLE
- A4 - AU Tax Invoice (INV) Email [email protected]
u
DARCY SIMPSON
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
FRAN MITCHELL
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
True
Environmental
QA/QC Compliance Assessment to assist with Quality ReviewWork Order : EB1709386 Page : 1 of 6
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL Telephone : +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017
Site : ---- Issue Date : 16-May-2017
DARCY SIMPSON:Sampler No. of samples received : 14
:Order number 1669283 No. of samples analysed : 14
This report is automatically generated by the ALS LIMS through interpretation of the ALS Quality Control Report and several Quality Assurance parameters measured by ALS. This automated
reporting highlights any non-conformances, facilitates faster and more accurate data validation and is designed to assist internal expert and external Auditor review. Many components of this
report contribute to the overall DQO assessment and reporting for guideline compliance.
Brief method summaries and references are also provided to assist in traceability.
Summary of Outliers
Outliers : Quality Control Samples
This report highlights outliers flagged in the Quality Control (QC) Report.
l NO Method Blank value outliers occur.
l NO Duplicate outliers occur.
l NO Laboratory Control outliers occur.
l NO Matrix Spike outliers occur.
l For all regular sample matrices, NO surrogate recovery outliers occur.
Outliers : Analysis Holding Time Compliance
l NO Analysis Holding Time Outliers exist.
Outliers : Frequency of Quality Control Samples
l NO Quality Control Sample Frequency Outliers exist.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
2 of 6:Page
Work Order :
:Client
EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Analysis Holding Time Compliance
Holding times for VOC in soils vary according to analytes of interest. Vinyl Chloride and Styrene holding time is 7 days; others 14 days. A recorded breach does not guarantee a breach for all VOC analytes and
should be verified in case the reported breach is a false positive or Vinyl Chloride and Styrene are not key analytes of interest/concern.
Holding time for leachate methods (e.g. TCLP) vary according to the analytes reported. Assessment compares the leach date with the shortest analyte holding time for the equivalent soil method. These are: organics
14 days, mercury 28 days & other metals 180 days. A recorded breach does not guarantee a breach for all non-volatile parameters.
If samples are identified below as having been analysed or extracted outside of recommended holding times, this should be taken into consideration when interpreting results.
This report summarizes extraction / preparation and analysis times and compares each with ALS recommended holding times (referencing USEPA SW 846, APHA, AS and NEPM) based on the sample container
provided. Dates reported represent first date of extraction or analysis and preclude subsequent dilutions and reruns. A listing of breaches (if any) is provided herein.
Matrix: SOIL Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EA055: Moisture Content
HDPE Soil Jar (EA055-103)
1218_SD001_0.0_170504, 1218_SD002_0.0_170504,
1218_SD003_0.0_170504, 1218_SD004_0.0_170504,
1218_SD005_0.0_170504, 1218_QC102_170504
18-May-2017---- 12-May-2017----04-May-2017 ---- ü
HDPE Soil Jar (EA055-103)
1218_SD006_0.0_170505, 1218_SD007_0.0_170505,
1218_SD008_0.0_170505, 1218_SD009_0.0_170505,
1218_SD010_0.0_170505, 1218_SD011_0.0_170505,
1218_SD012_0.0_170505
19-May-2017---- 12-May-2017----05-May-2017 ---- ü
EP231A: Perfluoroalkyl Sulfonic Acids
HDPE Soil Jar (EP231X)
1218_SD001_0.0_170504, 1218_SD002_0.0_170504,
1218_SD003_0.0_170504, 1218_SD004_0.0_170504,
1218_SD005_0.0_170504, 1218_QC102_170504
22-Jun-201731-Oct-2017 13-May-201713-May-201704-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_SD006_0.0_170505, 1218_SD007_0.0_170505,
1218_SD008_0.0_170505, 1218_SD009_0.0_170505,
1218_SD010_0.0_170505, 1218_SD011_0.0_170505,
1218_SD012_0.0_170505
22-Jun-201701-Nov-2017 13-May-201713-May-201705-May-2017 ü ü
EP231B: Perfluoroalkyl Carboxylic Acids
HDPE Soil Jar (EP231X)
1218_SD001_0.0_170504, 1218_SD002_0.0_170504,
1218_SD003_0.0_170504, 1218_SD004_0.0_170504,
1218_SD005_0.0_170504, 1218_QC102_170504
22-Jun-201731-Oct-2017 13-May-201713-May-201704-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_SD006_0.0_170505, 1218_SD007_0.0_170505,
1218_SD008_0.0_170505, 1218_SD009_0.0_170505,
1218_SD010_0.0_170505, 1218_SD011_0.0_170505,
1218_SD012_0.0_170505
22-Jun-201701-Nov-2017 13-May-201713-May-201705-May-2017 ü ü
3 of 6:Page
Work Order :
:Client
EB1709386
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Matrix: SOIL Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231C: Perfluoroalkyl Sulfonamides
HDPE Soil Jar (EP231X)
1218_SD001_0.0_170504, 1218_SD002_0.0_170504,
1218_SD003_0.0_170504, 1218_SD004_0.0_170504,
1218_SD005_0.0_170504, 1218_QC102_170504
22-Jun-201731-Oct-2017 13-May-201713-May-201704-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_SD006_0.0_170505, 1218_SD007_0.0_170505,
1218_SD008_0.0_170505, 1218_SD009_0.0_170505,
1218_SD010_0.0_170505, 1218_SD011_0.0_170505,
1218_SD012_0.0_170505
22-Jun-201701-Nov-2017 13-May-201713-May-201705-May-2017 ü ü
EP231D: (n:2) Fluorotelomer Sulfonic Acids
HDPE Soil Jar (EP231X)
1218_SD001_0.0_170504, 1218_SD002_0.0_170504,
1218_SD003_0.0_170504, 1218_SD004_0.0_170504,
1218_SD005_0.0_170504, 1218_QC102_170504
22-Jun-201731-Oct-2017 13-May-201713-May-201704-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_SD006_0.0_170505, 1218_SD007_0.0_170505,
1218_SD008_0.0_170505, 1218_SD009_0.0_170505,
1218_SD010_0.0_170505, 1218_SD011_0.0_170505,
1218_SD012_0.0_170505
22-Jun-201701-Nov-2017 13-May-201713-May-201705-May-2017 ü ü
EP231P: PFAS Sums
HDPE Soil Jar (EP231X)
1218_SD001_0.0_170504, 1218_SD002_0.0_170504,
1218_SD003_0.0_170504, 1218_SD004_0.0_170504,
1218_SD005_0.0_170504, 1218_QC102_170504
22-Jun-201731-Oct-2017 13-May-201713-May-201704-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_SD006_0.0_170505, 1218_SD007_0.0_170505,
1218_SD008_0.0_170505, 1218_SD009_0.0_170505,
1218_SD010_0.0_170505, 1218_SD011_0.0_170505,
1218_SD012_0.0_170505
22-Jun-201701-Nov-2017 13-May-201713-May-201705-May-2017 ü ü
Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231A: Perfluoroalkyl Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_QC301_170504 31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü üEP231B: Perfluoroalkyl Carboxylic Acids
HDPE (no PTFE) (EP231X-LL)
1218_QC301_170504 31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü üEP231C: Perfluoroalkyl Sulfonamides
HDPE (no PTFE) (EP231X-LL)
1218_QC301_170504 31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü ü
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Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231D: (n:2) Fluorotelomer Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_QC301_170504 31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü üEP231P: PFAS Sums
HDPE (no PTFE) (EP231X-LL)
1218_QC301_170504 31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü ü
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Quality Control Parameter Frequency ComplianceThe following report summarises the frequency of laboratory QC samples analysed within the analytical lot(s) in which the submitted sample(s) was(were) processed. Actual rate should be greater than or equal to
the expected rate. A listing of breaches is provided in the Summary of Outliers.
Matrix: SOIL Evaluation: û = Quality Control frequency not within specification ; ü = Quality Control frequency within specification.
Quality Control SpecificationQuality Control Sample Type
ExpectedQC Regular Actual
Rate (%)Quality Control Sample Type CountEvaluationAnalytical Methods Method
Laboratory Duplicates (DUP)
NEPM 2013 B3 & ALS QC Standard 10.26 10.004 39 üMoisture Content EA055-103
NEPM 2013 B3 & ALS QC Standard 10.00 10.002 20 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Laboratory Control Samples (LCS)
NEPM 2013 B3 & ALS QC Standard 5.00 5.001 20 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Method Blanks (MB)
NEPM 2013 B3 & ALS QC Standard 5.00 5.001 20 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Matrix Spikes (MS)
NEPM 2013 B3 & ALS QC Standard 5.00 5.001 20 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Matrix: WATER Evaluation: û = Quality Control frequency not within specification ; ü = Quality Control frequency within specification.
Quality Control SpecificationQuality Control Sample Type
ExpectedQC Regular Actual
Rate (%)Quality Control Sample Type CountEvaluationAnalytical Methods Method
Laboratory Duplicates (DUP)
NEPM 2013 B3 & ALS QC Standard 14.29 10.002 14 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Laboratory Control Samples (LCS)
NEPM 2013 B3 & ALS QC Standard 7.14 5.001 14 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Method Blanks (MB)
NEPM 2013 B3 & ALS QC Standard 7.14 5.001 14 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Matrix Spikes (MS)
NEPM 2013 B3 & ALS QC Standard 7.14 5.001 14 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
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Brief Method SummariesThe analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the US EPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request. The following report provides brief descriptions of the analytical procedures employed for results reported in the
Certificate of Analysis. Sources from which ALS methods have been developed are provided within the Method Descriptions.
Analytical Methods Method DescriptionsMatrixMethod
In house: A gravimetric procedure based on weight loss over a 12 hour drying period at 103-105 degrees C.
This method is compliant with NEPM (2013) Schedule B(3) Section 7.1 and Table 1 (14 day holding time).
Moisture Content EA055-103 SOIL
In-House. A portion of soil is extracted with MTBE. The extract is taken to dryness, made up in mobile phase.
Analysis is by LC/MSMS, ESI Negative Mode using MRM. PFOS is quantified using a certified, traceable standard
consisting of linear and branched PFOS isomers.
Per- and Polyfluoroalkyl Substances
(PFAS) by LCMSMS
EP231X SOIL
In-house: Analysis of fresh and saline waters by solid phase extraction followed by and LC-Electrospray-MS-MS,
Negative Mode using MRM. PFOS is quantified using a certified, traceable standard consisting of linear and
branched PFOS isomers.
Per- and Polyfluoroalkyl Substances
(PFAS by LCMSMS
EP231X-LL WATER
Preparation Methods Method DescriptionsMatrixMethod
In houseSample Extraction for PFAS EP231-PR SOIL
In houseSPE preparation for LL and saline PFCs EP231-SPE WATER
0 0.00 True
Environmental
CERTIFICATE OF ANALYSISWork Order : Page : 1 of 11EB1709386
:: LaboratoryClient GOLDER ASSOCIATES Environmental Division Brisbane
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia 4053
:Telephone +61 07 3721 5400 :Telephone +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017 09:00
:Order number 1669283 Date Analysis Commenced : 12-May-2017
:C-O-C number ---- Issue Date : 16-May-2017 16:32
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
14:No. of samples received
14:No. of samples analysed
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Certificate of Analysis contains the following information:
l General Comments
l Analytical Results
l Surrogate Control Limits
Additional information pertinent to this report will be found in the following separate attachments: Quality Control Report, QA/QC Compliance Assessment to assist with
Quality Review and Sample Receipt Notification.
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
Edwandy Fadjar Organic Coordinator Sydney Inorganics, Smithfield, NSW
Lana Nguyen Senior LCMS Chemist Sydney Organics, Smithfield, NSW
R I G H T S O L U T I O N S | R I G H T P A R T N E R
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General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis.
Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
When no sampling time is provided, the sampling time will default 00:00 on the date of sampling. If no sampling date is provided, the sampling date will be assumed by the laboratory and displayed in brackets without a
time component.
Where a result is required to meet compliance limits the associated uncertainty must be considered. Refer to the ALS Contact for details.
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
^ = This result is computed from individual analyte detections at or above the level of reporting
ø = ALS is not NATA accredited for these tests.
~ = Indicates an estimated value.
Key :
Analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site No. 10911 (Micro site no. 14913).l
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Analytical Results
1218_SD005_0.0_170
504
1218_SD004_0.0_170
504
1218_SD003_0.0_170
504
1218_SD002_0.0_170
504
1218_SD001_0.0_170
504
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
[04-May-2017][04-May-2017][04-May-2017][04-May-2017][04-May-2017]Client sampling date / time
EB1709386-005EB1709386-004EB1709386-003EB1709386-002EB1709386-001UnitLORCAS NumberCompound
Result Result Result Result Result
EA055: Moisture Content
19.2 16.7 10.5 7.3 26.6%1----Moisture Content (dried @ 103°C)
EP231A: Perfluoroalkyl Sulfonic Acids
<0.0002Perfluorobutane sulfonic acid
(PFBS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-73-5
<0.0002Perfluoropentane sulfonic acid
(PFPeS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-91-4
<0.0002Perfluorohexane sulfonic acid
(PFHxS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002355-46-4
<0.0002Perfluoroheptane sulfonic acid
(PFHpS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-92-8
0.0019Perfluorooctane sulfonic acid
(PFOS)
0.0015 0.0030 0.0006 0.0005mg/kg0.00021763-23-1
0.0004Perfluorodecane sulfonic acid
(PFDS)
0.0003 0.0003 <0.0002 <0.0002mg/kg0.0002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.001Perfluorobutanoic acid (PFBA) <0.001 <0.001 <0.001 <0.001mg/kg0.001375-22-4
<0.0002Perfluoropentanoic acid (PFPeA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-90-3
<0.0002Perfluorohexanoic acid (PFHxA) <0.0002 0.0003 <0.0002 <0.0002mg/kg0.0002307-24-4
<0.0002Perfluoroheptanoic acid (PFHpA) <0.0002 0.0003 <0.0002 <0.0002mg/kg0.0002375-85-9
<0.0002Perfluorooctanoic acid (PFOA) <0.0002 0.0004 <0.0002 <0.0002mg/kg0.0002335-67-1
<0.0002Perfluorononanoic acid (PFNA) <0.0002 0.0005 <0.0002 <0.0002mg/kg0.0002375-95-1
<0.0002Perfluorodecanoic acid (PFDA) <0.0002 0.0003 <0.0002 <0.0002mg/kg0.0002335-76-2
<0.0002Perfluoroundecanoic acid
(PFUnDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022058-94-8
<0.0002Perfluorododecanoic acid
(PFDoDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-55-1
<0.0002Perfluorotridecanoic acid
(PFTrDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.000272629-94-8
<0.0005Perfluorotetradecanoic acid
(PFTeDA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.0002Perfluorooctane sulfonamide
(FOSA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002754-91-6
<0.0005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000531506-32-8
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Analytical Results
1218_SD005_0.0_170
504
1218_SD004_0.0_170
504
1218_SD003_0.0_170
504
1218_SD002_0.0_170
504
1218_SD001_0.0_170
504
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
[04-May-2017][04-May-2017][04-May-2017][04-May-2017][04-May-2017]Client sampling date / time
EB1709386-005EB1709386-004EB1709386-003EB1709386-002EB1709386-001UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.0005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00054151-50-2
<0.0005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00052448-09-7
<0.0005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00051691-99-2
<0.0002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022355-31-9
<0.0002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.00054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005757124-72-4
<0.00056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000527619-97-2
<0.00058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000539108-34-4
<0.000510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005120226-60-0
EP231P: PFAS Sums
0.0023 0.0018 0.0051 0.0006 0.0005mg/kg0.0002----Sum of PFAS
0.0019Sum of PFHxS and PFOS 0.0015 0.0030 0.0006 0.0005mg/kg0.0002355-46-4/1763-23-
1
0.0019 0.0015 0.0040 0.0006 0.0005mg/kg0.0002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
93.4 105 95.1 100 96.7%0.0002----13C4-PFOS
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Analytical Results
1218_SD010_0.0_170
505
1218_SD009_0.0_170
505
1218_SD008_0.0_170
505
1218_SD007_0.0_170
505
1218_SD006_0.0_170
505
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
[05-May-2017][05-May-2017][05-May-2017][05-May-2017][05-May-2017]Client sampling date / time
EB1709386-010EB1709386-009EB1709386-008EB1709386-007EB1709386-006UnitLORCAS NumberCompound
Result Result Result Result Result
EA055: Moisture Content
22.7 59.0 2.7 38.6 3.6%1----Moisture Content (dried @ 103°C)
EP231A: Perfluoroalkyl Sulfonic Acids
<0.0002Perfluorobutane sulfonic acid
(PFBS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-73-5
<0.0002Perfluoropentane sulfonic acid
(PFPeS)
0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-91-4
<0.0002Perfluorohexane sulfonic acid
(PFHxS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002355-46-4
<0.0002Perfluoroheptane sulfonic acid
(PFHpS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-92-8
<0.0002Perfluorooctane sulfonic acid
(PFOS)
0.0010 <0.0002 <0.0002 0.0010mg/kg0.00021763-23-1
<0.0002Perfluorodecane sulfonic acid
(PFDS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.001Perfluorobutanoic acid (PFBA) <0.001 <0.001 <0.001 <0.001mg/kg0.001375-22-4
<0.0002Perfluoropentanoic acid (PFPeA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-90-3
<0.0002Perfluorohexanoic acid (PFHxA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-24-4
<0.0002Perfluoroheptanoic acid (PFHpA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-85-9
<0.0002Perfluorooctanoic acid (PFOA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-67-1
<0.0002Perfluorononanoic acid (PFNA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-95-1
<0.0002Perfluorodecanoic acid (PFDA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-76-2
<0.0002Perfluoroundecanoic acid
(PFUnDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022058-94-8
<0.0002Perfluorododecanoic acid
(PFDoDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-55-1
<0.0002Perfluorotridecanoic acid
(PFTrDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.000272629-94-8
<0.0005Perfluorotetradecanoic acid
(PFTeDA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.0002Perfluorooctane sulfonamide
(FOSA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002754-91-6
<0.0005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000531506-32-8
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Analytical Results
1218_SD010_0.0_170
505
1218_SD009_0.0_170
505
1218_SD008_0.0_170
505
1218_SD007_0.0_170
505
1218_SD006_0.0_170
505
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
[05-May-2017][05-May-2017][05-May-2017][05-May-2017][05-May-2017]Client sampling date / time
EB1709386-010EB1709386-009EB1709386-008EB1709386-007EB1709386-006UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.0005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00054151-50-2
<0.0005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00052448-09-7
<0.0005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00051691-99-2
<0.0002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022355-31-9
<0.0002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.00054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005757124-72-4
<0.00056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000527619-97-2
<0.00058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000539108-34-4
<0.000510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005120226-60-0
EP231P: PFAS Sums
<0.0002 0.0012 <0.0002 <0.0002 0.0010mg/kg0.0002----Sum of PFAS
<0.0002Sum of PFHxS and PFOS 0.0010 <0.0002 <0.0002 0.0010mg/kg0.0002355-46-4/1763-23-
1
<0.0002 0.0010 <0.0002 <0.0002 0.0010mg/kg0.0002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
84.7 95.9 96.3 101 95.8%0.0002----13C4-PFOS
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Analytical Results
--------1218_SD012_0.0_170
505
1218_SD011_0.0_170
505
1218_QC102_170504Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
--------[05-May-2017][05-May-2017][04-May-2017]Client sampling date / time
----------------EB1709386-014EB1709386-013EB1709386-011UnitLORCAS NumberCompound
Result Result Result ---- ----
EA055: Moisture Content
8.8 29.8 19.6 ---- ----%1----Moisture Content (dried @ 103°C)
EP231A: Perfluoroalkyl Sulfonic Acids
<0.0002Perfluorobutane sulfonic acid
(PFBS)
<0.0002 <0.0002 ---- ----mg/kg0.0002375-73-5
<0.0002Perfluoropentane sulfonic acid
(PFPeS)
<0.0002 <0.0002 ---- ----mg/kg0.00022706-91-4
<0.0002Perfluorohexane sulfonic acid
(PFHxS)
<0.0002 <0.0002 ---- ----mg/kg0.0002355-46-4
<0.0002Perfluoroheptane sulfonic acid
(PFHpS)
<0.0002 <0.0002 ---- ----mg/kg0.0002375-92-8
0.0010Perfluorooctane sulfonic acid
(PFOS)
<0.0002 <0.0002 ---- ----mg/kg0.00021763-23-1
<0.0002Perfluorodecane sulfonic acid
(PFDS)
<0.0002 <0.0002 ---- ----mg/kg0.0002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.001Perfluorobutanoic acid (PFBA) <0.001 <0.001 ---- ----mg/kg0.001375-22-4
<0.0002Perfluoropentanoic acid (PFPeA) <0.0002 <0.0002 ---- ----mg/kg0.00022706-90-3
<0.0002Perfluorohexanoic acid (PFHxA) <0.0002 <0.0002 ---- ----mg/kg0.0002307-24-4
<0.0002Perfluoroheptanoic acid (PFHpA) <0.0002 <0.0002 ---- ----mg/kg0.0002375-85-9
<0.0002Perfluorooctanoic acid (PFOA) <0.0002 <0.0002 ---- ----mg/kg0.0002335-67-1
<0.0002Perfluorononanoic acid (PFNA) <0.0002 <0.0002 ---- ----mg/kg0.0002375-95-1
<0.0002Perfluorodecanoic acid (PFDA) <0.0002 <0.0002 ---- ----mg/kg0.0002335-76-2
<0.0002Perfluoroundecanoic acid
(PFUnDA)
<0.0002 <0.0002 ---- ----mg/kg0.00022058-94-8
<0.0002Perfluorododecanoic acid
(PFDoDA)
<0.0002 <0.0002 ---- ----mg/kg0.0002307-55-1
<0.0002Perfluorotridecanoic acid
(PFTrDA)
<0.0002 <0.0002 ---- ----mg/kg0.000272629-94-8
<0.0005Perfluorotetradecanoic acid
(PFTeDA)
<0.0005 <0.0005 ---- ----mg/kg0.0005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.0002Perfluorooctane sulfonamide
(FOSA)
<0.0002 <0.0002 ---- ----mg/kg0.0002754-91-6
<0.0005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.0005 <0.0005 ---- ----mg/kg0.000531506-32-8
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Analytical Results
--------1218_SD012_0.0_170
505
1218_SD011_0.0_170
505
1218_QC102_170504Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
--------[05-May-2017][05-May-2017][04-May-2017]Client sampling date / time
----------------EB1709386-014EB1709386-013EB1709386-011UnitLORCAS NumberCompound
Result Result Result ---- ----
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.0005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.0005 <0.0005 ---- ----mg/kg0.00054151-50-2
<0.0005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.0005 <0.0005 ---- ----mg/kg0.00052448-09-7
<0.0005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.0005 <0.0005 ---- ----mg/kg0.00051691-99-2
<0.0002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.0002 <0.0002 ---- ----mg/kg0.00022355-31-9
<0.0002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.0002 <0.0002 ---- ----mg/kg0.00022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.00054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.0005 <0.0005 ---- ----mg/kg0.0005757124-72-4
<0.00056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.0005 <0.0005 ---- ----mg/kg0.000527619-97-2
<0.00058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.0005 <0.0005 ---- ----mg/kg0.000539108-34-4
<0.000510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.0005 <0.0005 ---- ----mg/kg0.0005120226-60-0
EP231P: PFAS Sums
0.0010 <0.0002 <0.0002 ---- ----mg/kg0.0002----Sum of PFAS
0.0010Sum of PFHxS and PFOS <0.0002 <0.0002 ---- ----mg/kg0.0002355-46-4/1763-23-
1
0.0010 <0.0002 <0.0002 ---- ----mg/kg0.0002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
94.6 99.0 91.3 ---- ----%0.0002----13C4-PFOS
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Analytical Results
----------------1218_QC301_170504Client sample IDSub-Matrix: WATER
(Matrix: WATER)
----------------[04-May-2017]Client sampling date / time
--------------------------------EB1709386-012UnitLORCAS NumberCompound
Result ---- ---- ---- ----
EP231A: Perfluoroalkyl Sulfonic Acids
<0.002Perfluorobutane sulfonic acid
(PFBS)
---- ---- ---- ----µg/L0.002375-73-5
<0.002Perfluoropentane sulfonic acid
(PFPeS)
---- ---- ---- ----µg/L0.0022706-91-4
<0.002Perfluorohexane sulfonic acid
(PFHxS)
---- ---- ---- ----µg/L0.002355-46-4
<0.002Perfluoroheptane sulfonic acid
(PFHpS)
---- ---- ---- ----µg/L0.002375-92-8
<0.002Perfluorooctane sulfonic acid
(PFOS)
---- ---- ---- ----µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
---- ---- ---- ----µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) ---- ---- ---- ----µg/L0.01375-22-4
<0.002Perfluoropentanoic acid (PFPeA) ---- ---- ---- ----µg/L0.0022706-90-3
<0.002Perfluorohexanoic acid (PFHxA) ---- ---- ---- ----µg/L0.002307-24-4
<0.002Perfluoroheptanoic acid (PFHpA) ---- ---- ---- ----µg/L0.002375-85-9
<0.002Perfluorooctanoic acid (PFOA) ---- ---- ---- ----µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) ---- ---- ---- ----µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) ---- ---- ---- ----µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
---- ---- ---- ----µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
---- ---- ---- ----µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
---- ---- ---- ----µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
---- ---- ---- ----µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
---- ---- ---- ----µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
---- ---- ---- ----µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
---- ---- ---- ----µg/L0.0054151-50-2
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Analytical Results
----------------1218_QC301_170504Client sample IDSub-Matrix: WATER
(Matrix: WATER)
----------------[04-May-2017]Client sampling date / time
--------------------------------EB1709386-012UnitLORCAS NumberCompound
Result ---- ---- ---- ----
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
---- ---- ---- ----µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
---- ---- ---- ----µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
---- ---- ---- ----µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
---- ---- ---- ----µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
---- ---- ---- ----µg/L0.005757124-72-4
<0.0056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
---- ---- ---- ----µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
---- ---- ---- ----µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
---- ---- ---- ----µg/L0.005120226-60-0
EP231P: PFAS Sums
<0.002 ---- ---- ---- ----µg/L0.002----Sum of PFAS
<0.002Sum of PFHxS and PFOS ---- ---- ---- ----µg/L0.002355-46-4/1763-23-
1
<0.002 ---- ---- ---- ----µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
99.3 ---- ---- ---- ----%0.002----13C4-PFOS
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Surrogate Control Limits
Recovery Limits (%)Sub-Matrix: SOIL
Compound CAS Number Low High
EP231S: PFAS Surrogate
13C4-PFOS ---- 70 130
Recovery Limits (%)Sub-Matrix: WATER
Compound CAS Number Low High
EP231S: PFAS Surrogate
13C4-PFOS ---- 70 120
False
1 1.00True
Environmental
QUALITY CONTROL REPORTWork Order : EB1709387 Page : 1 of 7
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL :Contact Matt Frost
:Address 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
Address : 2 Byth Street Stafford QLD Australia 4053
::Telephone +61 07 3721 5400 +61-7-3243 7222:Telephone
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017
:Order number 1669283 Date Analysis Commenced : 15-May-2017
:C-O-C number ---- Issue Date : 16-May-2017
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
No. of samples received 8:
No. of samples analysed 8:
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Quality Control Report contains the following information:
l Laboratory Duplicate (DUP) Report; Relative Percentage Difference (RPD) and Acceptance Limits
l Method Blank (MB) and Laboratory Control Spike (LCS) Report ; Recovery and Acceptance Limits
l Matrix Spike (MS) Report; Recovery and Acceptance Limits
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
R I G H T S O L U T I O N S | R I G H T P A R T N E R
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General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis. Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
Anonymous = Refers to samples which are not specifically part of this work order but formed part of the QC process lot
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
RPD = Relative Percentage Difference
# = Indicates failed QC
Key :
Laboratory Duplicate (DUP) Report
The quality control term Laboratory Duplicate refers to a randomly selected intralaboratory split. Laboratory duplicates provide information regarding method precision and sample heterogeneity. The permitted ranges
for the Relative Percent Deviation (RPD) of Laboratory Duplicates are specified in ALS Method QWI -EN/38 and are dependent on the magnitude of results in comparison to the level of reporting: Result < 10 times LOR:
No Limit; Result between 10 and 20 times LOR: 0% - 50%; Result > 20 times LOR: 0% - 20%.
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 883549)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L 0.013 0.013 0.00 No Limit1218_MW010_S_170504 EB1709387-001
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L 0.014 0.014 0.00 No Limit
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L 0.050 0.050 0.00 0% - 20%
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L 0.004 0.004 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L 0.036 0.037 0.00 0% - 50%
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 <0.002 0.00 No LimitAnonymous EB1709388-003
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 883549)
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_MW010_S_170504 EB1709387-001
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L 0.005 0.005 0.00 No Limit
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Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 883549) - continued
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_MW010_S_170504 EB1709387-001
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L 0.004 0.004 0.00 No Limit
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 <0.002 0.00 No LimitAnonymous EB1709388-003
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 883549)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_MW010_S_170504 EB1709387-001
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No LimitAnonymous EB1709388-003
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 <0.002 0.00 No Limit
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Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 883549) - continued
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No LimitAnonymous EB1709388-003
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QC Lot: 883549)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No Limit1218_MW010_S_170504 EB1709387-001
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No LimitAnonymous EB1709388-003
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
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Method Blank (MB) and Laboratory Control Spike (LCS) Report
The quality control term Method / Laboratory Blank refers to an analyte free matrix to which all reagents are added in the same volumes or proportions as used in standard sample preparation. The purpose of this QC
parameter is to monitor potential laboratory contamination. The quality control term Laboratory Control Spike (LCS) refers to a certified reference material, or a known interference free matrix spiked with target
analytes. The purpose of this QC parameter is to monitor method precision and accuracy independent of sample matrix. Dynamic Recovery Limits are based on statistical evaluation of processed LCS.
Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 883549)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 1050.05 µg/L 13060
EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.002 µg/L <0.002 1020.05 µg/L 13060
EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.002 µg/L <0.002 1160.05 µg/L 13060
EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.002 µg/L <0.002 74.40.05 µg/L 13060
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 883549)
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 84.20.25 µg/L 13060
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 85.20.05 µg/L 13060
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 85.20.05 µg/L 13060
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 85.00.05 µg/L 13060
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 1020.05 µg/L 13060
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 74.80.05 µg/L 13060
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 72.00.05 µg/L 13060
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 66.60.05 µg/L 13060
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 93.00.05 µg/L 13060
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 1180.05 µg/L 13060
EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.005 µg/L <0.005 88.80.125 µg/L 13060
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883549)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 1170.05 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.005 µg/L <0.005 94.50.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 4151-50-2 0.005 µg/L <0.005 97.10.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
2448-09-7 0.005 µg/L <0.005 82.20.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
1691-99-2 0.005 µg/L <0.005 94.20.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoacetic
acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 60.00.05 µg/L 13060
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883549)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 757124-72-4 0.005 µg/L <0.005 89.60.05 µg/L 13060
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 27619-97-2 0.005 µg/L <0.005 91.20.05 µg/L 13060
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Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883549) - continued
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 39108-34-4 0.005 µg/L <0.005 1020.05 µg/L 13060
EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 120226-60-0 0.005 µg/L <0.005 86.40.05 µg/L 13060
Matrix Spike (MS) ReportThe quality control term Matrix Spike (MS) refers to an intralaboratory split sample spiked with a representative set of target analytes. The purpose of this QC parameter is to monitor potential matrix effects on
analyte recoveries. Static Recovery Limits as per laboratory Data Quality Objectives (DQOs). Ideal recovery ranges stated may be waived in the event of sample matrix interference.
Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 883549)
1218_MW018_S_170504 EB1709387-003 375-73-5EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 1180.05 µg/L 13050
2706-91-4EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 91.20.05 µg/L 13050
355-46-4EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 1010.05 µg/L 13050
375-92-8EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 87.40.05 µg/L 13050
1763-23-1EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 85.40.05 µg/L 13050
335-77-3EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 80.40.05 µg/L 13050
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 883549)
1218_MW018_S_170504 EB1709387-003 375-22-4EP231X-LL: Perfluorobutanoic acid (PFBA) 65.40.25 µg/L 13030
2706-90-3EP231X-LL: Perfluoropentanoic acid (PFPeA) 70.20.05 µg/L 13050
307-24-4EP231X-LL: Perfluorohexanoic acid (PFHxA) 79.60.05 µg/L 13050
375-85-9EP231X-LL: Perfluoroheptanoic acid (PFHpA) 75.20.05 µg/L 13050
335-67-1EP231X-LL: Perfluorooctanoic acid (PFOA) 85.40.05 µg/L 13050
375-95-1EP231X-LL: Perfluorononanoic acid (PFNA) 62.60.05 µg/L 13050
335-76-2EP231X-LL: Perfluorodecanoic acid (PFDA) 67.60.05 µg/L 13050
2058-94-8EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 99.20.05 µg/L 13050
307-55-1EP231X-LL: Perfluorododecanoic acid (PFDoDA) 64.80.05 µg/L 13050
72629-94-8EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 89.60.05 µg/L 13030
376-06-7EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 91.40.125 µg/L 13030
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883549)
1218_MW018_S_170504 EB1709387-003 754-91-6EP231X-LL: Perfluorooctane sulfonamide (FOSA) 98.40.05 µg/L 13050
31506-32-8EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
94.90.125 µg/L 13030
4151-50-2EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
1040.125 µg/L 13030
2448-09-7EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
85.60.125 µg/L 13030
1691-99-2EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
87.80.125 µg/L 13030
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Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883549) - continued
1218_MW018_S_170504 EB1709387-003 2355-31-9EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
89.20.05 µg/L 13040
2991-50-6EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
71.20.05 µg/L 13040
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883549)
1218_MW018_S_170504 EB1709387-003 757124-72-4EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 73.20.05 µg/L 13050
27619-97-2EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 70.80.05 µg/L 13050
39108-34-4EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 72.40.05 µg/L 13050
120226-60-0EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 85.40.05 µg/L 13050
Environmental
SAMPLE RECEIPT NOTIFICATION (SRN)Work Order : EB1709387
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia
4053
:: E-mailE-mail [email protected] [email protected]
:: TelephoneTelephone +61 07 3721 5400 +61-7-3243 7222
:: FacsimileFacsimile +61 07 3721 5401 +61-7-3243 7218
::Project 1669283 Phase: 9202 Page 1 of 2
:Order number 1669283 :Quote number ES2016GOLASS0005 (EN/002/16 v2)
:C-O-C number ---- :QC Level NEPM 2013 B3 & ALS QC Standard
Site : ----
Sampler : DARCY SIMPSON
DatesDate Samples Received : Issue Date : 09-May-201709-May-2017 09:00
Scheduled Reporting Date: 16-May-2017:Client Requested Due
Date
16-May-2017
Delivery DetailsMode of Delivery : :Carrier Intact.Security Seal
No. of coolers/boxes : :1 Temperature 4.5°C - Ice present
: : 8 / 8MEDIUM ESKYReceipt Detail No. of samples received / analysed
General Comments
This report contains the following information:l
- Sample Container(s)/Preservation Non-Compliances
- Summary of Sample(s) and Requested Analysis
- Proactive Holding Time Report
- Requested Deliverables
l Discounted Package Prices apply only when specific ALS Group Codes ('W', 'S', 'NT' suites) are referenced on COCs.
l Analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site No.
10911 (Micro site no. 14913).l Please direct any turn around / technical queries to the laboratory contact designated above.
l Sample Disposal - Aqueous (14 days), Solid (60 days) from date of completion of work order.
l Breaches in recommended extraction / analysis holding times (if any) are displayed overleaf in
the Proactive Holding Time Report table.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
:Client GOLDER ASSOCIATES
Work Order : EB1709387 Amendment 02 of 2:Page
09-May-2017:Issue Date
Sample Container(s)/Preservation Non-Compliances
All comparisons are made against pretreatment/preservation AS, APHA, USEPA standards.
l No sample container / preservation non-compliance exists.
Summary of Sample(s) and Requested Analysis
Some items described below may be part of a laboratory
process necessary for the execution of client requested
tasks. Packages may contain additional analyses, such
as the determination of moisture content and preparation
tasks, that are included in the package.
If no sampling time is provided, the sampling time will
default 00:00 on the date of sampling. If no sampling date
is provided, the sampling date will be assumed by the
laboratory and displayed in brackets without a time
component
WA
TE
R -
EP
231X
-LL
PF
AS
- F
ull
Su
ite L
ow
Leve
l (2
8 a
naly
tes)
EB1709387-001 04-May-2017 00:00 1218_MW010_S_170504 ü
EB1709387-002 [ 05-May-2017 ] 1218_MW014_S_170505 ü
EB1709387-003 04-May-2017 00:00 1218_MW018_S_170504 ü
EB1709387-004 04-May-2017 00:00 1218_MW019_S_170504 ü
EB1709387-005 04-May-2017 00:00 1218_W001_S_170504 ü
EB1709387-006 04-May-2017 00:00 1218_W002_S_170504 ü
EB1709387-007 04-May-2017 00:00 1218_QC103_S_170504 ü
EB1709387-008 04-May-2017 00:00 1218_QC302_S_170505 ü
Matrix: WATER
Client sample IDLaboratory sample
ID
Client sampling
date / time
Proactive Holding Time Report
Sample(s) have been received within the recommended holding times for the requested analysis.
Requested Deliverables
ACCOUNTS PAYABLE
- A4 - AU Tax Invoice (INV) Email [email protected]
u
DARCY SIMPSON
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
FRAN MITCHELL
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
True
Environmental
QA/QC Compliance Assessment to assist with Quality ReviewWork Order : EB1709387 Page : 1 of 5
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL Telephone : +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017
Site : ---- Issue Date : 16-May-2017
DARCY SIMPSON:Sampler No. of samples received : 8
:Order number 1669283 No. of samples analysed : 8
This report is automatically generated by the ALS LIMS through interpretation of the ALS Quality Control Report and several Quality Assurance parameters measured by ALS. This automated
reporting highlights any non-conformances, facilitates faster and more accurate data validation and is designed to assist internal expert and external Auditor review. Many components of this
report contribute to the overall DQO assessment and reporting for guideline compliance.
Brief method summaries and references are also provided to assist in traceability.
Summary of Outliers
Outliers : Quality Control Samples
This report highlights outliers flagged in the Quality Control (QC) Report.
l NO Method Blank value outliers occur.
l NO Duplicate outliers occur.
l NO Laboratory Control outliers occur.
l NO Matrix Spike outliers occur.
l For all regular sample matrices, NO surrogate recovery outliers occur.
Outliers : Analysis Holding Time Compliance
l NO Analysis Holding Time Outliers exist.
Outliers : Frequency of Quality Control Samples
l NO Quality Control Sample Frequency Outliers exist.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
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Analysis Holding Time Compliance
Holding times for VOC in soils vary according to analytes of interest. Vinyl Chloride and Styrene holding time is 7 days; others 14 days. A recorded breach does not guarantee a breach for all VOC analytes and
should be verified in case the reported breach is a false positive or Vinyl Chloride and Styrene are not key analytes of interest/concern.
Holding time for leachate methods (e.g. TCLP) vary according to the analytes reported. Assessment compares the leach date with the shortest analyte holding time for the equivalent soil method. These are: organics
14 days, mercury 28 days & other metals 180 days. A recorded breach does not guarantee a breach for all non-volatile parameters.
If samples are identified below as having been analysed or extracted outside of recommended holding times, this should be taken into consideration when interpreting results.
This report summarizes extraction / preparation and analysis times and compares each with ALS recommended holding times (referencing USEPA SW 846, APHA, AS and NEPM) based on the sample container
provided. Dates reported represent first date of extraction or analysis and preclude subsequent dilutions and reruns. A listing of breaches (if any) is provided herein.
Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231A: Perfluoroalkyl Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_MW010_S_170504, 1218_MW018_S_170504,
1218_MW019_S_170504, 1218_W001_S_170504,
1218_W002_S_170504, 1218_QC103_S_170504,
1218_QC302_S_170505
31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü ü
HDPE (no PTFE) (EP231X-LL)
1218_MW014_S_170505 01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü üEP231B: Perfluoroalkyl Carboxylic Acids
HDPE (no PTFE) (EP231X-LL)
1218_MW010_S_170504, 1218_MW018_S_170504,
1218_MW019_S_170504, 1218_W001_S_170504,
1218_W002_S_170504, 1218_QC103_S_170504,
1218_QC302_S_170505
31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü ü
HDPE (no PTFE) (EP231X-LL)
1218_MW014_S_170505 01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü üEP231C: Perfluoroalkyl Sulfonamides
HDPE (no PTFE) (EP231X-LL)
1218_MW010_S_170504, 1218_MW018_S_170504,
1218_MW019_S_170504, 1218_W001_S_170504,
1218_W002_S_170504, 1218_QC103_S_170504,
1218_QC302_S_170505
31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü ü
HDPE (no PTFE) (EP231X-LL)
1218_MW014_S_170505 01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü üEP231D: (n:2) Fluorotelomer Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_MW010_S_170504, 1218_MW018_S_170504,
1218_MW019_S_170504, 1218_W001_S_170504,
1218_W002_S_170504, 1218_QC103_S_170504,
1218_QC302_S_170505
31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü ü
HDPE (no PTFE) (EP231X-LL)
1218_MW014_S_170505 01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü ü
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1669283 Phase: 9202:Project
Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231P: PFAS Sums
HDPE (no PTFE) (EP231X-LL)
1218_MW010_S_170504, 1218_MW018_S_170504,
1218_MW019_S_170504, 1218_W001_S_170504,
1218_W002_S_170504, 1218_QC103_S_170504,
1218_QC302_S_170505
31-Oct-201731-Oct-2017 15-May-201715-May-201704-May-2017 ü ü
HDPE (no PTFE) (EP231X-LL)
1218_MW014_S_170505 01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü ü
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1669283 Phase: 9202:Project
Quality Control Parameter Frequency ComplianceThe following report summarises the frequency of laboratory QC samples analysed within the analytical lot(s) in which the submitted sample(s) was(were) processed. Actual rate should be greater than or equal to
the expected rate. A listing of breaches is provided in the Summary of Outliers.
Matrix: WATER Evaluation: û = Quality Control frequency not within specification ; ü = Quality Control frequency within specification.
Quality Control SpecificationQuality Control Sample Type
ExpectedQC Regular Actual
Rate (%)Quality Control Sample Type CountEvaluationAnalytical Methods Method
Laboratory Duplicates (DUP)
NEPM 2013 B3 & ALS QC Standard 13.33 10.002 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Laboratory Control Samples (LCS)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Method Blanks (MB)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Matrix Spikes (MS)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
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Brief Method SummariesThe analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the US EPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request. The following report provides brief descriptions of the analytical procedures employed for results reported in the
Certificate of Analysis. Sources from which ALS methods have been developed are provided within the Method Descriptions.
Analytical Methods Method DescriptionsMatrixMethod
In-house: Analysis of fresh and saline waters by solid phase extraction followed by and LC-Electrospray-MS-MS,
Negative Mode using MRM. PFOS is quantified using a certified, traceable standard consisting of linear and
branched PFOS isomers.
Per- and Polyfluoroalkyl Substances
(PFAS by LCMSMS
EP231X-LL WATER
Preparation Methods Method DescriptionsMatrixMethod
In houseSPE preparation for LL and saline PFCs EP231-SPE WATER
0 0.00 True
Environmental
CERTIFICATE OF ANALYSISWork Order : Page : 1 of 7EB1709387
:: LaboratoryClient GOLDER ASSOCIATES Environmental Division Brisbane
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia 4053
:Telephone +61 07 3721 5400 :Telephone +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017 09:00
:Order number 1669283 Date Analysis Commenced : 15-May-2017
:C-O-C number ---- Issue Date : 16-May-2017 16:32
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
8:No. of samples received
8:No. of samples analysed
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Certificate of Analysis contains the following information:
l General Comments
l Analytical Results
l Surrogate Control Limits
Additional information pertinent to this report will be found in the following separate attachments: Quality Control Report, QA/QC Compliance Assessment to assist with
Quality Review and Sample Receipt Notification.
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
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General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis.
Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
When no sampling time is provided, the sampling time will default 00:00 on the date of sampling. If no sampling date is provided, the sampling date will be assumed by the laboratory and displayed in brackets without a
time component.
Where a result is required to meet compliance limits the associated uncertainty must be considered. Refer to the ALS Contact for details.
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
^ = This result is computed from individual analyte detections at or above the level of reporting
ø = ALS is not NATA accredited for these tests.
~ = Indicates an estimated value.
Key :
Analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site No. 10911 (Micro site no. 14913).l
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GOLDER ASSOCIATES
Analytical Results
1218_W001_S_17050
4
1218_MW019_S_1705
04
1218_MW018_S_1705
04
1218_MW014_S_1705
05
1218_MW010_S_1705
04
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
04-May-2017 00:0004-May-2017 00:0004-May-2017 00:00[05-May-2017]04-May-2017 00:00Client sampling date / time
EB1709387-005EB1709387-004EB1709387-003EB1709387-002EB1709387-001UnitLORCAS NumberCompound
Result Result Result Result Result
EP231A: Perfluoroalkyl Sulfonic Acids
0.013Perfluorobutane sulfonic acid
(PFBS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-73-5
0.014Perfluoropentane sulfonic acid
(PFPeS)
<0.002 <0.002 0.002 <0.002µg/L0.0022706-91-4
0.050Perfluorohexane sulfonic acid
(PFHxS)
<0.002 0.006 0.008 <0.002µg/L0.002355-46-4
0.004Perfluoroheptane sulfonic acid
(PFHpS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-92-8
0.036Perfluorooctane sulfonic acid
(PFOS)
0.026 0.034 <0.002 <0.002µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
<0.002 <0.002 <0.002 <0.002µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) <0.01 <0.01 <0.01 <0.01µg/L0.01375-22-4
<0.002Perfluoropentanoic acid (PFPeA) <0.002 <0.002 <0.002 <0.002µg/L0.0022706-90-3
0.005Perfluorohexanoic acid (PFHxA) <0.002 <0.002 <0.002 <0.002µg/L0.002307-24-4
<0.002Perfluoroheptanoic acid (PFHpA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-85-9
0.004Perfluorooctanoic acid (PFOA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
<0.002 <0.002 <0.002 <0.002µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
<0.002 <0.002 <0.002 <0.002µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
<0.005 <0.005 <0.005 <0.005µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
<0.002 <0.002 <0.002 <0.002µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.0054151-50-2
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Work Order :
:Client
EB1709387
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_W001_S_17050
4
1218_MW019_S_1705
04
1218_MW018_S_1705
04
1218_MW014_S_1705
05
1218_MW010_S_1705
04
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
04-May-2017 00:0004-May-2017 00:0004-May-2017 00:00[05-May-2017]04-May-2017 00:00Client sampling date / time
EB1709387-005EB1709387-004EB1709387-003EB1709387-002EB1709387-001UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005757124-72-4
<0.0056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005120226-60-0
EP231P: PFAS Sums
0.126 0.026 0.040 0.010 <0.002µg/L0.002----Sum of PFAS
0.086Sum of PFHxS and PFOS 0.026 0.040 0.008 <0.002µg/L0.002355-46-4/1763-23-
1
0.086 <0.002 0.006 0.010 <0.002µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
109 107 110 111 108%0.002----13C4-PFOS
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GOLDER ASSOCIATES
Analytical Results
--------1218_QC302_S_1705
05
1218_QC103_S_1705
04
1218_W002_S_17050
4
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
--------04-May-2017 00:0004-May-2017 00:0004-May-2017 00:00Client sampling date / time
----------------EB1709387-008EB1709387-007EB1709387-006UnitLORCAS NumberCompound
Result Result Result ---- ----
EP231A: Perfluoroalkyl Sulfonic Acids
<0.002Perfluorobutane sulfonic acid
(PFBS)
<0.002 <0.002 ---- ----µg/L0.002375-73-5
<0.002Perfluoropentane sulfonic acid
(PFPeS)
<0.002 <0.002 ---- ----µg/L0.0022706-91-4
<0.002Perfluorohexane sulfonic acid
(PFHxS)
<0.002 <0.002 ---- ----µg/L0.002355-46-4
<0.002Perfluoroheptane sulfonic acid
(PFHpS)
<0.002 <0.002 ---- ----µg/L0.002375-92-8
<0.002Perfluorooctane sulfonic acid
(PFOS)
<0.002 <0.002 ---- ----µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
<0.002 <0.002 ---- ----µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) <0.01 <0.01 ---- ----µg/L0.01375-22-4
<0.002Perfluoropentanoic acid (PFPeA) <0.002 <0.002 ---- ----µg/L0.0022706-90-3
<0.002Perfluorohexanoic acid (PFHxA) <0.002 <0.002 ---- ----µg/L0.002307-24-4
<0.002Perfluoroheptanoic acid (PFHpA) <0.002 <0.002 ---- ----µg/L0.002375-85-9
<0.002Perfluorooctanoic acid (PFOA) <0.002 <0.002 ---- ----µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) <0.002 <0.002 ---- ----µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) <0.002 <0.002 ---- ----µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
<0.002 <0.002 ---- ----µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
<0.002 <0.002 ---- ----µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
<0.002 <0.002 ---- ----µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
<0.005 <0.005 ---- ----µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
<0.002 <0.002 ---- ----µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.005 <0.005 ---- ----µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.005 <0.005 ---- ----µg/L0.0054151-50-2
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EB1709387
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
--------1218_QC302_S_1705
05
1218_QC103_S_1705
04
1218_W002_S_17050
4
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
--------04-May-2017 00:0004-May-2017 00:0004-May-2017 00:00Client sampling date / time
----------------EB1709387-008EB1709387-007EB1709387-006UnitLORCAS NumberCompound
Result Result Result ---- ----
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.005 <0.005 ---- ----µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.005 <0.005 ---- ----µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.002 <0.002 ---- ----µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.002 <0.002 ---- ----µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.005 <0.005 ---- ----µg/L0.005757124-72-4
<0.0056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.005 <0.005 ---- ----µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.005 <0.005 ---- ----µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.005 <0.005 ---- ----µg/L0.005120226-60-0
EP231P: PFAS Sums
<0.002 <0.002 <0.002 ---- ----µg/L0.002----Sum of PFAS
<0.002Sum of PFHxS and PFOS <0.002 <0.002 ---- ----µg/L0.002355-46-4/1763-23-
1
<0.002 <0.002 <0.002 ---- ----µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
108 113 106 ---- ----%0.002----13C4-PFOS
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Surrogate Control Limits
Recovery Limits (%)Sub-Matrix: WATER
Compound CAS Number Low High
EP231S: PFAS Surrogate
13C4-PFOS ---- 70 120
False
1 1.00True
Environmental
QUALITY CONTROL REPORTWork Order : EB1709388 Page : 1 of 7
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL :Contact Matt Frost
:Address 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
Address : 2 Byth Street Stafford QLD Australia 4053
::Telephone +61 07 3721 5400 +61-7-3243 7222:Telephone
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017
:Order number 1669283 Date Analysis Commenced : 15-May-2017
:C-O-C number ---- Issue Date : 16-May-2017
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
No. of samples received 7:
No. of samples analysed 7:
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Quality Control Report contains the following information:
l Laboratory Duplicate (DUP) Report; Relative Percentage Difference (RPD) and Acceptance Limits
l Method Blank (MB) and Laboratory Control Spike (LCS) Report ; Recovery and Acceptance Limits
l Matrix Spike (MS) Report; Recovery and Acceptance Limits
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
R I G H T S O L U T I O N S | R I G H T P A R T N E R
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General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis. Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
Anonymous = Refers to samples which are not specifically part of this work order but formed part of the QC process lot
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
RPD = Relative Percentage Difference
# = Indicates failed QC
Key :
Laboratory Duplicate (DUP) Report
The quality control term Laboratory Duplicate refers to a randomly selected intralaboratory split. Laboratory duplicates provide information regarding method precision and sample heterogeneity. The permitted ranges
for the Relative Percent Deviation (RPD) of Laboratory Duplicates are specified in ALS Method QWI -EN/38 and are dependent on the magnitude of results in comparison to the level of reporting: Result < 10 times LOR:
No Limit; Result between 10 and 20 times LOR: 0% - 50%; Result > 20 times LOR: 0% - 20%.
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 883549)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L 0.013 0.013 0.00 No LimitAnonymous EB1709387-001
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L 0.014 0.014 0.00 No Limit
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L 0.050 0.050 0.00 0% - 20%
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L 0.004 0.004 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L 0.036 0.037 0.00 0% - 50%
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_SW009_S_170505 EB1709388-003
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 883549)
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 <0.002 0.00 No LimitAnonymous EB1709387-001
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L 0.005 0.005 0.00 No Limit
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1669283 Phase: 9202:Project
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 883549) - continued
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 <0.002 0.00 No LimitAnonymous EB1709387-001
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L 0.004 0.004 0.00 No Limit
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_SW009_S_170505 EB1709388-003
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 883549)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No LimitAnonymous EB1709387-001
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_SW009_S_170505 EB1709388-003
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 <0.002 0.00 No Limit
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1669283 Phase: 9202:Project
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 883549) - continued
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No Limit1218_SW009_S_170505 EB1709388-003
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QC Lot: 883549)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No LimitAnonymous EB1709387-001
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No Limit1218_SW009_S_170505 EB1709388-003
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
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Method Blank (MB) and Laboratory Control Spike (LCS) Report
The quality control term Method / Laboratory Blank refers to an analyte free matrix to which all reagents are added in the same volumes or proportions as used in standard sample preparation. The purpose of this QC
parameter is to monitor potential laboratory contamination. The quality control term Laboratory Control Spike (LCS) refers to a certified reference material, or a known interference free matrix spiked with target
analytes. The purpose of this QC parameter is to monitor method precision and accuracy independent of sample matrix. Dynamic Recovery Limits are based on statistical evaluation of processed LCS.
Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 883549)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 1050.05 µg/L 13060
EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.002 µg/L <0.002 1020.05 µg/L 13060
EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.002 µg/L <0.002 1160.05 µg/L 13060
EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.002 µg/L <0.002 74.40.05 µg/L 13060
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 883549)
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 84.20.25 µg/L 13060
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 85.20.05 µg/L 13060
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 85.20.05 µg/L 13060
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 85.00.05 µg/L 13060
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 1020.05 µg/L 13060
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 74.80.05 µg/L 13060
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 72.00.05 µg/L 13060
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 66.60.05 µg/L 13060
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 93.00.05 µg/L 13060
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 1180.05 µg/L 13060
EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.005 µg/L <0.005 88.80.125 µg/L 13060
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883549)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 1170.05 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.005 µg/L <0.005 94.50.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 4151-50-2 0.005 µg/L <0.005 97.10.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
2448-09-7 0.005 µg/L <0.005 82.20.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
1691-99-2 0.005 µg/L <0.005 94.20.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoacetic
acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 60.00.05 µg/L 13060
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883549)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 757124-72-4 0.005 µg/L <0.005 89.60.05 µg/L 13060
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 27619-97-2 0.005 µg/L <0.005 91.20.05 µg/L 13060
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Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883549) - continued
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 39108-34-4 0.005 µg/L <0.005 1020.05 µg/L 13060
EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 120226-60-0 0.005 µg/L <0.005 86.40.05 µg/L 13060
Matrix Spike (MS) ReportThe quality control term Matrix Spike (MS) refers to an intralaboratory split sample spiked with a representative set of target analytes. The purpose of this QC parameter is to monitor potential matrix effects on
analyte recoveries. Static Recovery Limits as per laboratory Data Quality Objectives (DQOs). Ideal recovery ranges stated may be waived in the event of sample matrix interference.
Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 883549)
Anonymous EB1709387-003 375-73-5EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 1180.05 µg/L 13050
2706-91-4EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 91.20.05 µg/L 13050
355-46-4EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 1010.05 µg/L 13050
375-92-8EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 87.40.05 µg/L 13050
1763-23-1EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 85.40.05 µg/L 13050
335-77-3EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 80.40.05 µg/L 13050
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 883549)
Anonymous EB1709387-003 375-22-4EP231X-LL: Perfluorobutanoic acid (PFBA) 65.40.25 µg/L 13030
2706-90-3EP231X-LL: Perfluoropentanoic acid (PFPeA) 70.20.05 µg/L 13050
307-24-4EP231X-LL: Perfluorohexanoic acid (PFHxA) 79.60.05 µg/L 13050
375-85-9EP231X-LL: Perfluoroheptanoic acid (PFHpA) 75.20.05 µg/L 13050
335-67-1EP231X-LL: Perfluorooctanoic acid (PFOA) 85.40.05 µg/L 13050
375-95-1EP231X-LL: Perfluorononanoic acid (PFNA) 62.60.05 µg/L 13050
335-76-2EP231X-LL: Perfluorodecanoic acid (PFDA) 67.60.05 µg/L 13050
2058-94-8EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 99.20.05 µg/L 13050
307-55-1EP231X-LL: Perfluorododecanoic acid (PFDoDA) 64.80.05 µg/L 13050
72629-94-8EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 89.60.05 µg/L 13030
376-06-7EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 91.40.125 µg/L 13030
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883549)
Anonymous EB1709387-003 754-91-6EP231X-LL: Perfluorooctane sulfonamide (FOSA) 98.40.05 µg/L 13050
31506-32-8EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
94.90.125 µg/L 13030
4151-50-2EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
1040.125 µg/L 13030
2448-09-7EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
85.60.125 µg/L 13030
1691-99-2EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
87.80.125 µg/L 13030
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Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 883549) - continued
Anonymous EB1709387-003 2355-31-9EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
89.20.05 µg/L 13040
2991-50-6EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
71.20.05 µg/L 13040
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 883549)
Anonymous EB1709387-003 757124-72-4EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 73.20.05 µg/L 13050
27619-97-2EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 70.80.05 µg/L 13050
39108-34-4EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 72.40.05 µg/L 13050
120226-60-0EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 85.40.05 µg/L 13050
True
Environmental
QA/QC Compliance Assessment to assist with Quality ReviewWork Order : EB1709388 Page : 1 of 4
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL Telephone : +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017
Site : ---- Issue Date : 16-May-2017
DARCY SIMPSON:Sampler No. of samples received : 7
:Order number 1669283 No. of samples analysed : 7
This report is automatically generated by the ALS LIMS through interpretation of the ALS Quality Control Report and several Quality Assurance parameters measured by ALS. This automated
reporting highlights any non-conformances, facilitates faster and more accurate data validation and is designed to assist internal expert and external Auditor review. Many components of this
report contribute to the overall DQO assessment and reporting for guideline compliance.
Brief method summaries and references are also provided to assist in traceability.
Summary of Outliers
Outliers : Quality Control Samples
This report highlights outliers flagged in the Quality Control (QC) Report.
l NO Method Blank value outliers occur.
l NO Duplicate outliers occur.
l NO Laboratory Control outliers occur.
l NO Matrix Spike outliers occur.
l For all regular sample matrices, NO surrogate recovery outliers occur.
Outliers : Analysis Holding Time Compliance
l NO Analysis Holding Time Outliers exist.
Outliers : Frequency of Quality Control Samples
l NO Quality Control Sample Frequency Outliers exist.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
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Analysis Holding Time Compliance
Holding times for VOC in soils vary according to analytes of interest. Vinyl Chloride and Styrene holding time is 7 days; others 14 days. A recorded breach does not guarantee a breach for all VOC analytes and
should be verified in case the reported breach is a false positive or Vinyl Chloride and Styrene are not key analytes of interest/concern.
Holding time for leachate methods (e.g. TCLP) vary according to the analytes reported. Assessment compares the leach date with the shortest analyte holding time for the equivalent soil method. These are: organics
14 days, mercury 28 days & other metals 180 days. A recorded breach does not guarantee a breach for all non-volatile parameters.
If samples are identified below as having been analysed or extracted outside of recommended holding times, this should be taken into consideration when interpreting results.
This report summarizes extraction / preparation and analysis times and compares each with ALS recommended holding times (referencing USEPA SW 846, APHA, AS and NEPM) based on the sample container
provided. Dates reported represent first date of extraction or analysis and preclude subsequent dilutions and reruns. A listing of breaches (if any) is provided herein.
Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231A: Perfluoroalkyl Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_SW006_S_170505, 1218_SW007_S_170505,
1218_SW009_S_170505, 1218_QC101_170505,
1218_QC401_170505, 1218_SW011_S_170505,
1218_SW012_S_170505
01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü ü
EP231B: Perfluoroalkyl Carboxylic Acids
HDPE (no PTFE) (EP231X-LL)
1218_SW006_S_170505, 1218_SW007_S_170505,
1218_SW009_S_170505, 1218_QC101_170505,
1218_QC401_170505, 1218_SW011_S_170505,
1218_SW012_S_170505
01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü ü
EP231C: Perfluoroalkyl Sulfonamides
HDPE (no PTFE) (EP231X-LL)
1218_SW006_S_170505, 1218_SW007_S_170505,
1218_SW009_S_170505, 1218_QC101_170505,
1218_QC401_170505, 1218_SW011_S_170505,
1218_SW012_S_170505
01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü ü
EP231D: (n:2) Fluorotelomer Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_SW006_S_170505, 1218_SW007_S_170505,
1218_SW009_S_170505, 1218_QC101_170505,
1218_QC401_170505, 1218_SW011_S_170505,
1218_SW012_S_170505
01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü ü
EP231P: PFAS Sums
HDPE (no PTFE) (EP231X-LL)
1218_SW006_S_170505, 1218_SW007_S_170505,
1218_SW009_S_170505, 1218_QC101_170505,
1218_QC401_170505, 1218_SW011_S_170505,
1218_SW012_S_170505
01-Nov-201701-Nov-2017 15-May-201715-May-201705-May-2017 ü ü
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Quality Control Parameter Frequency ComplianceThe following report summarises the frequency of laboratory QC samples analysed within the analytical lot(s) in which the submitted sample(s) was(were) processed. Actual rate should be greater than or equal to
the expected rate. A listing of breaches is provided in the Summary of Outliers.
Matrix: WATER Evaluation: û = Quality Control frequency not within specification ; ü = Quality Control frequency within specification.
Quality Control SpecificationQuality Control Sample Type
ExpectedQC Regular Actual
Rate (%)Quality Control Sample Type CountEvaluationAnalytical Methods Method
Laboratory Duplicates (DUP)
NEPM 2013 B3 & ALS QC Standard 13.33 10.002 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Laboratory Control Samples (LCS)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Method Blanks (MB)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Matrix Spikes (MS)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
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Brief Method SummariesThe analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the US EPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request. The following report provides brief descriptions of the analytical procedures employed for results reported in the
Certificate of Analysis. Sources from which ALS methods have been developed are provided within the Method Descriptions.
Analytical Methods Method DescriptionsMatrixMethod
In-house: Analysis of fresh and saline waters by solid phase extraction followed by and LC-Electrospray-MS-MS,
Negative Mode using MRM. PFOS is quantified using a certified, traceable standard consisting of linear and
branched PFOS isomers.
Per- and Polyfluoroalkyl Substances
(PFAS by LCMSMS
EP231X-LL WATER
Preparation Methods Method DescriptionsMatrixMethod
In houseSPE preparation for LL and saline PFCs EP231-SPE WATER
0 0.00 True
Environmental
CERTIFICATE OF ANALYSISWork Order : Page : 1 of 7EB1709388
:: LaboratoryClient GOLDER ASSOCIATES Environmental Division Brisbane
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia 4053
:Telephone +61 07 3721 5400 :Telephone +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 09-May-2017 09:00
:Order number 1669283 Date Analysis Commenced : 15-May-2017
:C-O-C number ---- Issue Date : 16-May-2017 16:33
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
7:No. of samples received
7:No. of samples analysed
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Certificate of Analysis contains the following information:
l General Comments
l Analytical Results
l Surrogate Control Limits
Additional information pertinent to this report will be found in the following separate attachments: Quality Control Report, QA/QC Compliance Assessment to assist with
Quality Review and Sample Receipt Notification.
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
R I G H T S O L U T I O N S | R I G H T P A R T N E R
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General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis.
Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
When no sampling time is provided, the sampling time will default 00:00 on the date of sampling. If no sampling date is provided, the sampling date will be assumed by the laboratory and displayed in brackets without a
time component.
Where a result is required to meet compliance limits the associated uncertainty must be considered. Refer to the ALS Contact for details.
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
^ = This result is computed from individual analyte detections at or above the level of reporting
ø = ALS is not NATA accredited for these tests.
~ = Indicates an estimated value.
Key :
Analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site No. 10911 (Micro site no. 14913).l
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Analytical Results
1218_QC401_1705051218_QC101_1705051218_SW009_S_1705
05
1218_SW007_S_1705
05
1218_SW006_S_1705
05
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
[05-May-2017][05-May-2017][05-May-2017][05-May-2017][05-May-2017]Client sampling date / time
EB1709388-005EB1709388-004EB1709388-003EB1709388-002EB1709388-001UnitLORCAS NumberCompound
Result Result Result Result Result
EP231A: Perfluoroalkyl Sulfonic Acids
<0.002Perfluorobutane sulfonic acid
(PFBS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-73-5
<0.002Perfluoropentane sulfonic acid
(PFPeS)
<0.002 <0.002 <0.002 <0.002µg/L0.0022706-91-4
<0.002Perfluorohexane sulfonic acid
(PFHxS)
<0.002 <0.002 <0.002 <0.002µg/L0.002355-46-4
<0.002Perfluoroheptane sulfonic acid
(PFHpS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-92-8
<0.002Perfluorooctane sulfonic acid
(PFOS)
<0.002 <0.002 <0.002 <0.002µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
<0.002 <0.002 <0.002 <0.002µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) <0.01 <0.01 <0.01 <0.01µg/L0.01375-22-4
<0.002Perfluoropentanoic acid (PFPeA) <0.002 <0.002 <0.002 <0.002µg/L0.0022706-90-3
<0.002Perfluorohexanoic acid (PFHxA) <0.002 <0.002 <0.002 <0.002µg/L0.002307-24-4
<0.002Perfluoroheptanoic acid (PFHpA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-85-9
<0.002Perfluorooctanoic acid (PFOA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
<0.002 <0.002 <0.002 <0.002µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
<0.002 <0.002 <0.002 <0.002µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
<0.005 <0.005 <0.005 <0.005µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
<0.002 <0.002 <0.002 <0.002µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.0054151-50-2
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Analytical Results
1218_QC401_1705051218_QC101_1705051218_SW009_S_1705
05
1218_SW007_S_1705
05
1218_SW006_S_1705
05
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
[05-May-2017][05-May-2017][05-May-2017][05-May-2017][05-May-2017]Client sampling date / time
EB1709388-005EB1709388-004EB1709388-003EB1709388-002EB1709388-001UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005757124-72-4
<0.0056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005120226-60-0
EP231P: PFAS Sums
<0.002 <0.002 <0.002 <0.002 <0.002µg/L0.002----Sum of PFAS
<0.002Sum of PFHxS and PFOS <0.002 <0.002 <0.002 <0.002µg/L0.002355-46-4/1763-23-
1
<0.002 <0.002 <0.002 <0.002 <0.002µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
111 111 107 108 109%0.002----13C4-PFOS
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Analytical Results
------------1218_SW012_S_1705
05
1218_SW011_S_1705
05
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
------------[05-May-2017][05-May-2017]Client sampling date / time
------------------------EB1709388-007EB1709388-006UnitLORCAS NumberCompound
Result Result ---- ---- ----
EP231A: Perfluoroalkyl Sulfonic Acids
<0.002Perfluorobutane sulfonic acid
(PFBS)
<0.002 ---- ---- ----µg/L0.002375-73-5
<0.002Perfluoropentane sulfonic acid
(PFPeS)
<0.002 ---- ---- ----µg/L0.0022706-91-4
<0.002Perfluorohexane sulfonic acid
(PFHxS)
<0.002 ---- ---- ----µg/L0.002355-46-4
<0.002Perfluoroheptane sulfonic acid
(PFHpS)
<0.002 ---- ---- ----µg/L0.002375-92-8
<0.002Perfluorooctane sulfonic acid
(PFOS)
<0.002 ---- ---- ----µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
<0.002 ---- ---- ----µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) <0.01 ---- ---- ----µg/L0.01375-22-4
<0.002Perfluoropentanoic acid (PFPeA) <0.002 ---- ---- ----µg/L0.0022706-90-3
<0.002Perfluorohexanoic acid (PFHxA) <0.002 ---- ---- ----µg/L0.002307-24-4
<0.002Perfluoroheptanoic acid (PFHpA) <0.002 ---- ---- ----µg/L0.002375-85-9
<0.002Perfluorooctanoic acid (PFOA) <0.002 ---- ---- ----µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) <0.002 ---- ---- ----µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) <0.002 ---- ---- ----µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
<0.002 ---- ---- ----µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
<0.002 ---- ---- ----µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
<0.002 ---- ---- ----µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
<0.005 ---- ---- ----µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
<0.002 ---- ---- ----µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.005 ---- ---- ----µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.005 ---- ---- ----µg/L0.0054151-50-2
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Analytical Results
------------1218_SW012_S_1705
05
1218_SW011_S_1705
05
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
------------[05-May-2017][05-May-2017]Client sampling date / time
------------------------EB1709388-007EB1709388-006UnitLORCAS NumberCompound
Result Result ---- ---- ----
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.005 ---- ---- ----µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.005 ---- ---- ----µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.002 ---- ---- ----µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.002 ---- ---- ----µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.005 ---- ---- ----µg/L0.005757124-72-4
<0.0056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.005 ---- ---- ----µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.005 ---- ---- ----µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.005 ---- ---- ----µg/L0.005120226-60-0
EP231P: PFAS Sums
<0.002 <0.002 ---- ---- ----µg/L0.002----Sum of PFAS
<0.002Sum of PFHxS and PFOS <0.002 ---- ---- ----µg/L0.002355-46-4/1763-23-
1
<0.002 <0.002 ---- ---- ----µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
112 113 ---- ---- ----%0.002----13C4-PFOS
7 of 7:Page
Work Order :
:Client
EB1709388
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Surrogate Control Limits
Recovery Limits (%)Sub-Matrix: WATER
Compound CAS Number Low High
EP231S: PFAS Surrogate
13C4-PFOS ---- 70 120
Environmental
SAMPLE RECEIPT NOTIFICATION (SRN)Work Order : EB1709388
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia
4053
:: E-mailE-mail [email protected] [email protected]
:: TelephoneTelephone +61 07 3721 5400 +61-7-3243 7222
:: FacsimileFacsimile +61 07 3721 5401 +61-7-3243 7218
::Project 1669283 Phase: 9202 Page 1 of 2
:Order number 1669283 :Quote number ES2016GOLASS0005 (EN/002/16 v2)
:C-O-C number ---- :QC Level NEPM 2013 B3 & ALS QC Standard
Site : ----
Sampler : DARCY SIMPSON
DatesDate Samples Received : Issue Date : 09-May-201709-May-2017 09:00
Scheduled Reporting Date: 16-May-2017:Client Requested Due
Date
16-May-2017
Delivery DetailsMode of Delivery : :Carrier Intact.Security Seal
No. of coolers/boxes : :1 Temperature 4.5°C - Ice present
: : 7 / 7MEDIUM ESKYReceipt Detail No. of samples received / analysed
General Comments
This report contains the following information:l
- Sample Container(s)/Preservation Non-Compliances
- Summary of Sample(s) and Requested Analysis
- Proactive Holding Time Report
- Requested Deliverables
l Discounted Package Prices apply only when specific ALS Group Codes ('W', 'S', 'NT' suites) are referenced on COCs.
l Analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site No.
10911 (Micro site no. 14913).l Please direct any turn around / technical queries to the laboratory contact designated above.
l Sample Disposal - Aqueous (14 days), Solid (60 days) from date of completion of work order.
l Breaches in recommended extraction / analysis holding times (if any) are displayed overleaf in
the Proactive Holding Time Report table.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
:Client GOLDER ASSOCIATES
Work Order : EB1709388 Amendment 02 of 2:Page
09-May-2017:Issue Date
Sample Container(s)/Preservation Non-Compliances
All comparisons are made against pretreatment/preservation AS, APHA, USEPA standards.
l No sample container / preservation non-compliance exists.
Summary of Sample(s) and Requested Analysis
Some items described below may be part of a laboratory
process necessary for the execution of client requested
tasks. Packages may contain additional analyses, such
as the determination of moisture content and preparation
tasks, that are included in the package.
If no sampling time is provided, the sampling time will
default 00:00 on the date of sampling. If no sampling date
is provided, the sampling date will be assumed by the
laboratory and displayed in brackets without a time
component
WA
TE
R -
EP
231X
-LL
PF
AS
- F
ull
Su
ite L
ow
Leve
l (2
8 a
naly
tes)
EB1709388-001 [ 05-May-2017 ] 1218_SW006_S_170505 ü
EB1709388-002 [ 05-May-2017 ] 1218_SW007_S_170505 ü
EB1709388-003 [ 05-May-2017 ] 1218_SW009_S_170505 ü
EB1709388-004 [ 05-May-2017 ] 1218_QC101_170505 ü
EB1709388-005 [ 05-May-2017 ] 1218_QC401_170505 ü
EB1709388-006 [ 05-May-2017 ] 1218_SW011_S_170505 ü
EB1709388-007 [ 05-May-2017 ] 1218_SW012_S_170505 ü
Matrix: WATER
Client sample IDLaboratory sample
ID
Client sampling
date / time
Proactive Holding Time Report
Sample(s) have been received within the recommended holding times for the requested analysis.
Requested Deliverables
ACCOUNTS PAYABLE
- A4 - AU Tax Invoice (INV) Email [email protected]
u
DARCY SIMPSON
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
FRAN MITCHELL
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
False
2 2.00True
Environmental
QUALITY CONTROL REPORTWork Order : EB1710297 Page : 1 of 11
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL :Contact Matt Frost
:Address 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
Address : 2 Byth Street Stafford QLD Australia 4053
::Telephone +61 07 3721 5400 +61-7-3243 7222:Telephone
:Project 1669283 Phase: 9202 Date Samples Received : 19-May-2017
:Order number 1669286 Date Analysis Commenced : 23-May-2017
:C-O-C number ---- Issue Date : 26-May-2017
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
No. of samples received 52:
No. of samples analysed 34:
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Quality Control Report contains the following information:
l Laboratory Duplicate (DUP) Report; Relative Percentage Difference (RPD) and Acceptance Limits
l Method Blank (MB) and Laboratory Control Spike (LCS) Report ; Recovery and Acceptance Limits
l Matrix Spike (MS) Report; Recovery and Acceptance Limits
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
Edwandy Fadjar Organic Coordinator Sydney Inorganics, Smithfield, NSW
R I G H T S O L U T I O N S | R I G H T P A R T N E R
2 of 11:Page
Work Order :
:Client
EB1710297
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis. Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
Anonymous = Refers to samples which are not specifically part of this work order but formed part of the QC process lot
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
RPD = Relative Percentage Difference
# = Indicates failed QC
Key :
Laboratory Duplicate (DUP) Report
The quality control term Laboratory Duplicate refers to a randomly selected intralaboratory split. Laboratory duplicates provide information regarding method precision and sample heterogeneity. The permitted ranges
for the Relative Percent Deviation (RPD) of Laboratory Duplicates are specified in ALS Method QWI -EN/38 and are dependent on the magnitude of results in comparison to the level of reporting: Result < 10 times LOR:
No Limit; Result between 10 and 20 times LOR: 0% - 50%; Result > 20 times LOR: 0% - 20%.
Sub-Matrix: SOIL Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EA055: Moisture Content (QC Lot: 903985)
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 33.7 34.5 2.31 0% - 20%Anonymous EB1710253-001
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 9.8 10.2 3.15 0% - 50%1218_BH027_0.5-0.75_170
508
EB1710297-025
EA055: Moisture Content (QC Lot: 903986)
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 12.1 11.4 5.85 0% - 50%1218_BH022_11.5-11.75_1
70511
EB1710297-044
EA055-103: Moisture Content (dried @ 103°C) ---- 1 % 37.4 35.3 5.92 0% - 20%Anonymous EB1710304-018
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 904010)
EP231X: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_BH024_0.8-1.0_1705
12
EB1710297-010
EP231X: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_SD013_0.0_170509 EB1710297-036
EP231X: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.0002 mg/kg 0.0002 0.0002 0.00 No Limit
EP231X: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 904010)
EP231X: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_BH024_0.8-1.0_1705
12
EB1710297-010
EP231X: Perfluorohexanoic acid (PFHxA) 307-24-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
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Work Order :
:Client
EB1710297
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: SOIL Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 904010) - continued
EP231X: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_BH024_0.8-1.0_1705
12
EB1710297-010
EP231X: Perfluorooctanoic acid (PFOA) 335-67-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorononanoic acid (PFNA) 375-95-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorodecanoic acid (PFDA) 335-76-2 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: Perfluorobutanoic acid (PFBA) 375-22-4 0.001 mg/kg <0.001 <0.001 0.00 No Limit
EP231X: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_SD013_0.0_170509 EB1710297-036
EP231X: Perfluorohexanoic acid (PFHxA) 307-24-4 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorooctanoic acid (PFOA) 335-67-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorononanoic acid (PFNA) 375-95-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorodecanoic acid (PFDA) 335-76-2 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: Perfluorobutanoic acid (PFBA) 375-22-4 0.001 mg/kg <0.001 <0.001 0.00 No Limit
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 904010)
EP231X: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_BH024_0.8-1.0_1705
12
EB1710297-010
EP231X: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit1218_SD013_0.0_170509 EB1710297-036
EP231X: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
EP231X: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.0002 mg/kg <0.0002 <0.0002 0.00 No Limit
4 of 11:Page
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:Client
EB1710297
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: SOIL Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 904010) - continued
EP231X: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit1218_SD013_0.0_170509 EB1710297-036
EP231X: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QC Lot: 904010)
EP231X: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit1218_BH024_0.8-1.0_1705
12
EB1710297-010
EP231X: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 10:2 Fluorotelomer sulfonic acid (10:2
FTS)
120226-60-0 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit1218_SD013_0.0_170509 EB1710297-036
EP231X: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
EP231X: 10:2 Fluorotelomer sulfonic acid (10:2
FTS)
120226-60-0 0.0005 mg/kg <0.0005 <0.0005 0.00 No Limit
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 904743)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_MW026_S_170515 EB1710297-001
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_QC303_170508 EB1710297-033
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GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231A: Perfluoroalkyl Sulfonic Acids (QC Lot: 904743) - continued
EP231X-LL: Perfluoropentane sulfonic acid
(PFPeS)
2706-91-4 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_QC303_170508 EB1710297-033
EP231X-LL: Perfluorohexane sulfonic acid
(PFHxS)
355-46-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptane sulfonic acid
(PFHpS)
375-92-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonic acid
(PFOS)
1763-23-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecane sulfonic acid
(PFDS)
335-77-3 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231B: Perfluoroalkyl Carboxylic Acids (QC Lot: 904743)
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_MW026_S_170515 EB1710297-001
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_QC303_170508 EB1710297-033
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: Perfluorotetradecanoic acid
(PFTeDA)
376-06-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 <0.01 0.00 No Limit
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 904743)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_MW026_S_170515 EB1710297-001
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
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Sub-Matrix: WATER Laboratory Duplicate (DUP) Report
Original Result RPD (%)Laboratory sample ID Client sample ID Method: Compound CAS Number LOR Unit Duplicate Result Recovery Limits (%)
EP231C: Perfluoroalkyl Sulfonamides (QC Lot: 904743) - continued
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_MW026_S_170515 EB1710297-001
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 <0.002 0.00 No Limit1218_QC303_170508 EB1710297-033
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoacetic acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 <0.002 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamide (MeFOSA)
31506-32-8 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
4151-50-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
2448-09-7 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
1691-99-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QC Lot: 904743)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No Limit1218_MW026_S_170515 EB1710297-001
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2
FTS)
757124-72-4 0.005 µg/L <0.005 <0.005 0.00 No Limit1218_QC303_170508 EB1710297-033
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2
FTS)
27619-97-2 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2
FTS)
39108-34-4 0.005 µg/L <0.005 <0.005 0.00 No Limit
EP231X-LL: 10:2 Fluorotelomer sulfonic acid
(10:2 FTS)
120226-60-0 0.005 µg/L <0.005 <0.005 0.00 No Limit
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Method Blank (MB) and Laboratory Control Spike (LCS) Report
The quality control term Method / Laboratory Blank refers to an analyte free matrix to which all reagents are added in the same volumes or proportions as used in standard sample preparation. The purpose of this QC
parameter is to monitor potential laboratory contamination. The quality control term Laboratory Control Spike (LCS) refers to a certified reference material, or a known interference free matrix spiked with target
analytes. The purpose of this QC parameter is to monitor method precision and accuracy independent of sample matrix. Dynamic Recovery Limits are based on statistical evaluation of processed LCS.
Sub-Matrix: SOIL Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 904010)
EP231X: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.0002 mg/kg <0.0002 75.40.00125 mg/kg 12157
EP231X: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.0002 mg/kg <0.0002 75.20.00125 mg/kg 12555
EP231X: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.0002 mg/kg <0.0002 75.60.00125 mg/kg 12652
EP231X: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.0002 mg/kg <0.0002 81.60.00125 mg/kg 12354
EP231X: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.0002 mg/kg <0.0002 1050.00125 mg/kg 12755
EP231X: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.0002 mg/kg <0.0002 78.40.00125 mg/kg 12554
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 904010)
EP231X: Perfluorobutanoic acid (PFBA) 375-22-4 0.001 mg/kg <0.001 1010.00625 mg/kg 12852
EP231X: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.0002 mg/kg <0.0002 79.90.00125 mg/kg 12954
EP231X: Perfluorohexanoic acid (PFHxA) 307-24-4 0.0002 mg/kg <0.0002 77.00.00125 mg/kg 12758
EP231X: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.0002 mg/kg <0.0002 73.60.00125 mg/kg 12857
EP231X: Perfluorooctanoic acid (PFOA) 335-67-1 0.0002 mg/kg <0.0002 84.80.00125 mg/kg 13460
EP231X: Perfluorononanoic acid (PFNA) 375-95-1 0.0002 mg/kg <0.0002 81.80.00125 mg/kg 13063
EP231X: Perfluorodecanoic acid (PFDA) 335-76-2 0.0002 mg/kg <0.0002 70.00.00125 mg/kg 13055
EP231X: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.0002 mg/kg <0.0002 1030.00125 mg/kg 13062
EP231X: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.0002 mg/kg <0.0002 1070.00125 mg/kg 13453
EP231X: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.0002 mg/kg <0.0002 68.50.00125 mg/kg 12949
EP231X: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.0005 mg/kg <0.0005 1020.00312 mg/kg 12959
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 904010)
EP231X: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.0002 mg/kg <0.0002 80.90.00125 mg/kg 13252
EP231X: N-Methyl perfluorooctane sulfonamide (MeFOSA) 31506-32-8 0.0005 mg/kg <0.0005 97.60.00312 mg/kg 12665
EP231X: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 4151-50-2 0.0005 mg/kg <0.0005 98.90.00312 mg/kg 12664
EP231X: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
2448-09-7 0.0005 mg/kg <0.0005 1020.00312 mg/kg 12463
EP231X: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
1691-99-2 0.0005 mg/kg <0.0005 1110.00312 mg/kg 12558
EP231X: N-Methyl perfluorooctane sulfonamidoacetic acid
(MeFOSAA)
2355-31-9 0.0002 mg/kg <0.0002 70.40.00125 mg/kg 13061
EP231X: N-Ethyl perfluorooctane sulfonamidoacetic acid
(EtFOSAA)
2991-50-6 0.0002 mg/kg <0.0002 1020.00125 mg/kg 13055
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 904010)
EP231X: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 757124-72-4 0.0005 mg/kg <0.0005 80.00.00125 mg/kg 13054
EP231X: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 27619-97-2 0.0005 mg/kg <0.0005 65.80.00125 mg/kg 13061
EP231X: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 39108-34-4 0.0005 mg/kg <0.0005 71.80.00125 mg/kg 13062
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Sub-Matrix: SOIL Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 904010) - continued
EP231X: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 120226-60-0 0.0005 mg/kg <0.0005 86.40.00125 mg/kg 13060
Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 904743)
EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 375-73-5 0.002 µg/L <0.002 83.60.05 µg/L 13060
EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 2706-91-4 0.002 µg/L <0.002 85.60.05 µg/L 13060
EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 355-46-4 0.002 µg/L <0.002 80.20.05 µg/L 13060
EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 375-92-8 0.002 µg/L <0.002 85.80.05 µg/L 13060
EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 1763-23-1 0.002 µg/L <0.002 82.80.05 µg/L 13060
EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 335-77-3 0.002 µg/L <0.002 87.60.05 µg/L 13060
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 904743)
EP231X-LL: Perfluorobutanoic acid (PFBA) 375-22-4 0.01 µg/L <0.01 85.60.25 µg/L 13060
EP231X-LL: Perfluoropentanoic acid (PFPeA) 2706-90-3 0.002 µg/L <0.002 1060.05 µg/L 13060
EP231X-LL: Perfluorohexanoic acid (PFHxA) 307-24-4 0.002 µg/L <0.002 91.00.05 µg/L 13060
EP231X-LL: Perfluoroheptanoic acid (PFHpA) 375-85-9 0.002 µg/L <0.002 87.80.05 µg/L 13060
EP231X-LL: Perfluorooctanoic acid (PFOA) 335-67-1 0.002 µg/L <0.002 1010.05 µg/L 13060
EP231X-LL: Perfluorononanoic acid (PFNA) 375-95-1 0.002 µg/L <0.002 93.60.05 µg/L 13060
EP231X-LL: Perfluorodecanoic acid (PFDA) 335-76-2 0.002 µg/L <0.002 95.60.05 µg/L 13060
EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 2058-94-8 0.002 µg/L <0.002 97.40.05 µg/L 13060
EP231X-LL: Perfluorododecanoic acid (PFDoDA) 307-55-1 0.002 µg/L <0.002 75.00.05 µg/L 13060
EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 72629-94-8 0.002 µg/L <0.002 1000.05 µg/L 13060
EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 376-06-7 0.005 µg/L <0.005 1020.125 µg/L 13060
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 904743)
EP231X-LL: Perfluorooctane sulfonamide (FOSA) 754-91-6 0.002 µg/L <0.002 1150.05 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
31506-32-8 0.005 µg/L <0.005 85.40.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 4151-50-2 0.005 µg/L <0.005 82.50.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
2448-09-7 0.005 µg/L <0.005 91.10.125 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
1691-99-2 0.005 µg/L <0.005 95.80.125 µg/L 13060
EP231X-LL: N-Methyl perfluorooctane sulfonamidoacetic
acid (MeFOSAA)
2355-31-9 0.002 µg/L <0.002 92.20.05 µg/L 13060
EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
2991-50-6 0.002 µg/L <0.002 1000.05 µg/L 13060
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 904743)
EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 757124-72-4 0.005 µg/L <0.005 1080.05 µg/L 13060
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Sub-Matrix: WATER Method Blank (MB)
Report
Laboratory Control Spike (LCS) Report
Spike Spike Recovery (%) Recovery Limits (%)
Result Concentration HighLowLCSMethod: Compound CAS Number LOR Unit
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 904743) - continued
EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 27619-97-2 0.005 µg/L <0.005 90.60.05 µg/L 13060
EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 39108-34-4 0.005 µg/L <0.005 90.00.05 µg/L 13060
EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 120226-60-0 0.005 µg/L <0.005 78.20.05 µg/L 13060
Matrix Spike (MS) ReportThe quality control term Matrix Spike (MS) refers to an intralaboratory split sample spiked with a representative set of target analytes. The purpose of this QC parameter is to monitor potential matrix effects on
analyte recoveries. Static Recovery Limits as per laboratory Data Quality Objectives (DQOs). Ideal recovery ranges stated may be waived in the event of sample matrix interference.
Sub-Matrix: SOIL Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 904010)
1218_BH024_0.8-1.0_170512 EB1710297-010 375-73-5EP231X: Perfluorobutane sulfonic acid (PFBS) 55.50.00125 mg/kg 13050
2706-91-4EP231X: Perfluoropentane sulfonic acid (PFPeS) 57.90.00125 mg/kg 13050
355-46-4EP231X: Perfluorohexane sulfonic acid (PFHxS) 72.40.00125 mg/kg 13050
375-92-8EP231X: Perfluoroheptane sulfonic acid (PFHpS) 65.60.00125 mg/kg 13050
1763-23-1EP231X: Perfluorooctane sulfonic acid (PFOS) 77.90.00125 mg/kg 13050
335-77-3EP231X: Perfluorodecane sulfonic acid (PFDS) 67.80.00125 mg/kg 13050
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 904010)
1218_BH024_0.8-1.0_170512 EB1710297-010 375-22-4EP231X: Perfluorobutanoic acid (PFBA) 72.90.00625 mg/kg 13030
2706-90-3EP231X: Perfluoropentanoic acid (PFPeA) 89.70.00125 mg/kg 13050
307-24-4EP231X: Perfluorohexanoic acid (PFHxA) 63.00.00125 mg/kg 13050
375-85-9EP231X: Perfluoroheptanoic acid (PFHpA) 77.20.00125 mg/kg 13050
335-67-1EP231X: Perfluorooctanoic acid (PFOA) 85.80.00125 mg/kg 13050
375-95-1EP231X: Perfluorononanoic acid (PFNA) 78.90.00125 mg/kg 13050
335-76-2EP231X: Perfluorodecanoic acid (PFDA) 65.40.00125 mg/kg 13050
2058-94-8EP231X: Perfluoroundecanoic acid (PFUnDA) 1040.00125 mg/kg 13050
307-55-1EP231X: Perfluorododecanoic acid (PFDoDA) 1020.00125 mg/kg 13050
72629-94-8EP231X: Perfluorotridecanoic acid (PFTrDA) 74.00.00125 mg/kg 13030
376-06-7EP231X: Perfluorotetradecanoic acid (PFTeDA) 87.10.00312 mg/kg 13030
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 904010)
1218_BH024_0.8-1.0_170512 EB1710297-010 754-91-6EP231X: Perfluorooctane sulfonamide (FOSA) 60.50.00125 mg/kg 13050
31506-32-8EP231X: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
79.60.00312 mg/kg 13030
4151-50-2EP231X: N-Ethyl perfluorooctane sulfonamide (EtFOSA) 60.80.00312 mg/kg 13030
2448-09-7EP231X: N-Methyl perfluorooctane sulfonamidoethanol
(MeFOSE)
64.20.00312 mg/kg 13030
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Sub-Matrix: SOIL Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 904010) - continued
1218_BH024_0.8-1.0_170512 EB1710297-010 1691-99-2EP231X: N-Ethyl perfluorooctane sulfonamidoethanol
(EtFOSE)
69.50.00312 mg/kg 13030
2355-31-9EP231X: N-Methyl perfluorooctane sulfonamidoacetic
acid (MeFOSAA)
80.80.00125 mg/kg 13030
2991-50-6EP231X: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
1180.00125 mg/kg 13030
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 904010)
1218_BH024_0.8-1.0_170512 EB1710297-010 757124-72-4EP231X: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 79.00.00125 mg/kg 13050
27619-97-2EP231X: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 79.50.00125 mg/kg 13050
39108-34-4EP231X: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 64.00.00125 mg/kg 13050
120226-60-0EP231X: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 1030.00125 mg/kg 13050
Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231A: Perfluoroalkyl Sulfonic Acids (QCLot: 904743)
1218_MW027_S_170515 EB1710297-002 375-73-5EP231X-LL: Perfluorobutane sulfonic acid (PFBS) 1060.05 µg/L 13050
2706-91-4EP231X-LL: Perfluoropentane sulfonic acid (PFPeS) 95.60.05 µg/L 13050
355-46-4EP231X-LL: Perfluorohexane sulfonic acid (PFHxS) 75.20.05 µg/L 13050
375-92-8EP231X-LL: Perfluoroheptane sulfonic acid (PFHpS) 99.40.05 µg/L 13050
1763-23-1EP231X-LL: Perfluorooctane sulfonic acid (PFOS) 63.00.05 µg/L 13050
335-77-3EP231X-LL: Perfluorodecane sulfonic acid (PFDS) 71.40.05 µg/L 13050
EP231B: Perfluoroalkyl Carboxylic Acids (QCLot: 904743)
1218_MW027_S_170515 EB1710297-002 375-22-4EP231X-LL: Perfluorobutanoic acid (PFBA) 94.00.25 µg/L 13030
2706-90-3EP231X-LL: Perfluoropentanoic acid (PFPeA) 64.20.05 µg/L 13050
307-24-4EP231X-LL: Perfluorohexanoic acid (PFHxA) 82.80.05 µg/L 13050
375-85-9EP231X-LL: Perfluoroheptanoic acid (PFHpA) 68.80.05 µg/L 13050
335-67-1EP231X-LL: Perfluorooctanoic acid (PFOA) 88.80.05 µg/L 13050
375-95-1EP231X-LL: Perfluorononanoic acid (PFNA) 69.00.05 µg/L 13050
335-76-2EP231X-LL: Perfluorodecanoic acid (PFDA) 60.20.05 µg/L 13050
2058-94-8EP231X-LL: Perfluoroundecanoic acid (PFUnDA) 83.40.05 µg/L 13050
307-55-1EP231X-LL: Perfluorododecanoic acid (PFDoDA) 60.60.05 µg/L 13050
72629-94-8EP231X-LL: Perfluorotridecanoic acid (PFTrDA) 71.80.05 µg/L 13030
376-06-7EP231X-LL: Perfluorotetradecanoic acid (PFTeDA) 90.20.125 µg/L 13030
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 904743)
1218_MW027_S_170515 EB1710297-002 754-91-6EP231X-LL: Perfluorooctane sulfonamide (FOSA) 65.20.05 µg/L 13050
31506-32-8EP231X-LL: N-Methyl perfluorooctane sulfonamide
(MeFOSA)
95.20.125 µg/L 13030
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Sub-Matrix: WATER Matrix Spike (MS) Report
SpikeRecovery(%) Recovery Limits (%)Spike
HighLowMSConcentrationLaboratory sample ID Client sample ID Method: Compound CAS Number
EP231C: Perfluoroalkyl Sulfonamides (QCLot: 904743) - continued
1218_MW027_S_170515 EB1710297-002 4151-50-2EP231X-LL: N-Ethyl perfluorooctane sulfonamide
(EtFOSA)
76.70.125 µg/L 13030
2448-09-7EP231X-LL: N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
87.10.125 µg/L 13030
1691-99-2EP231X-LL: N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
92.70.125 µg/L 13030
2355-31-9EP231X-LL: N-Methyl perfluorooctane
sulfonamidoacetic acid (MeFOSAA)
54.80.05 µg/L 13040
2991-50-6EP231X-LL: N-Ethyl perfluorooctane sulfonamidoacetic
acid (EtFOSAA)
72.80.05 µg/L 13040
EP231D: (n:2) Fluorotelomer Sulfonic Acids (QCLot: 904743)
1218_MW027_S_170515 EB1710297-002 757124-72-4EP231X-LL: 4:2 Fluorotelomer sulfonic acid (4:2 FTS) 1120.05 µg/L 13050
27619-97-2EP231X-LL: 6:2 Fluorotelomer sulfonic acid (6:2 FTS) 82.20.05 µg/L 13050
39108-34-4EP231X-LL: 8:2 Fluorotelomer sulfonic acid (8:2 FTS) 57.20.05 µg/L 13050
120226-60-0EP231X-LL: 10:2 Fluorotelomer sulfonic acid (10:2 FTS) 72.00.05 µg/L 13050
Environmental
SAMPLE RECEIPT NOTIFICATION (SRN)Work Order : EB1710297
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia
4053
:: E-mailE-mail [email protected] [email protected]
:: TelephoneTelephone +61 07 3721 5400 +61-7-3243 7222
:: FacsimileFacsimile +61 07 3721 5401 +61-7-3243 7218
::Project 1669283 Phase: 9202 Page 1 of 4
:Order number ---- :Quote number ES2016GOLASS0005 (EN/002/16 v2)
:C-O-C number ---- :QC Level NEPM 2013 B3 & ALS QC Standard
Site : ----
Sampler : DARCY SIMPSON
DatesDate Samples Received : Issue Date : 19-May-201719-May-2017 13:20
Scheduled Reporting Date: 26-May-2017:Client Requested Due
Date
26-May-2017
Delivery DetailsMode of Delivery : :Carrier Intact.Security Seal
No. of coolers/boxes : :2 Temperature 4.4°C, 2.0°C - Ice present
: : 52 / 34MEDIUM ESKYReceipt Detail No. of samples received / analysed
General Comments
This report contains the following information:l
- Sample Container(s)/Preservation Non-Compliances
- Summary of Sample(s) and Requested Analysis
- Proactive Holding Time Report
- Requested Deliverables
l Please be advised that sample "1218_QC105_170513" was not received at the laboratory (denoted
SNR on the scanned COC).l Please be advised, where PFAS (EP231X-LL) analysis has been listed ON SOIL SAMPLES on the
submitted Chain of Custody, PFAS(EP231X) analysis has been assigned. If this is incorrect please
contact Client Services at [email protected] .l Discounted Package Prices apply only when specific ALS Group Codes ('W', 'S', 'NT' suites) are referenced on COCs.
l PFAS analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site
No. 10911 (Micro site no. 14913).l Please direct any turn around / technical queries to the laboratory contact designated above.
l Sample Disposal - Aqueous (14 days), Solid (60 days) from date of completion of work order.
l Breaches in recommended extraction / analysis holding times (if any) are displayed overleaf in
the Proactive Holding Time Report table.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
:Client GOLDER ASSOCIATES
Work Order : EB1710297 Amendment 02 of 4:Page
19-May-2017:Issue Date
Sample Container(s)/Preservation Non-Compliances
All comparisons are made against pretreatment/preservation AS, APHA, USEPA standards.
l No sample container / preservation non-compliance exists.
Any sample identifications that cannot be displayed entirely in the analysis summary table will be listed below.
EB1710297-010 : [ 12-May-2017 ] : 1218_BH024_0.8-1.0_170512
EB1710297-011 : [ 12-May-2017 ] : 1218_BH024_8.5-8.75_170512
EB1710297-015 : [ 10-May-2017 ] : 1218_BH025_0.6-0.75170510
EB1710297-018 : [ 11-May-2017 ] : 1218_BH025_16.5-16.75170511
EB1710297-025 : [ 08-May-2017 ] : 1218_BH027_0.5-0.75_170508
EB1710297-026 : [ 08-May-2017 ] : 1218_BH027_7.8-8.0_170508
EB1710297-028 : [ 09-May-2017 ] : 1218_BH026_0.6-0.75_170509
EB1710297-030 : [ 09-May-2017 ] : 1218_BH026_7.0-7.25_170509
EB1710297-036 : [ 09-May-2017 ] : 1218_SD013_0.0_170509
EB1710297-037 : [ 10-May-2017 ] : 1218_BH023_0.6-0.75_170510
EB1710297-040 : [ 10-May-2017 ] : 1218_BH023_13.8-14.0_170510
EB1710297-042 : [ 13-May-2017 ] : 1218_BH022_0.7-0.95_170511
EB1710297-044 : [ 13-May-2017 ] : 1218_BH022_11.5-11.75_170511
Summary of Sample(s) and Requested Analysis
Some items described below may be part of a laboratory
process necessary for the execution of client requested
tasks. Packages may contain additional analyses, such
as the determination of moisture content and preparation
tasks, that are included in the package.
If no sampling time is provided, the sampling time will
default 00:00 on the date of sampling. If no sampling date
is provided, the sampling date will be assumed by the
laboratory and displayed in brackets without a time
component
(On
Ho
ld)
SO
IL
No
an
aly
sis
req
ue
ste
d
SO
IL -
EA
05
5-1
03
Mo
istu
re C
on
ten
t
SO
IL -
EP
23
1X
(so
lids)
PF
AS
- F
ull
Su
ite (
28
an
aly
tes)
EB1710297-010 [ 12-May-2017 ] 1218_BH024_0.8-1.0_1... ü ü
EB1710297-011 [ 12-May-2017 ] 1218_BH024_8.5-8.75_... ü ü
EB1710297-012 [ 12-May-2017 ] 1218_BH024_12.5-12.7... ü
EB1710297-013 [ 12-May-2017 ] 1218_BH024_16.5-16.7... ü
EB1710297-014 12-May-2017 00:00 1218_BH024_21.5-21.7... ü
EB1710297-015 10-May-2017 00:00 1218_BH025_0.6-0.751... ü ü
EB1710297-016 11-May-2017 00:00 1218_BH025_7.5-7.75_... ü
EB1710297-017 11-May-2017 00:00 1218_BH025_11.5-11.7... ü
EB1710297-018 11-May-2017 00:00 1218_BH025_16.5-16.7... ü ü
EB1710297-019 11-May-2017 00:00 1218_BH025_22.25-22.... ü
EB1710297-020 11-May-2017 00:00 1218_QC106_170511 ü
EB1710297-023 12-May-2017 00:00 1218_QC107_170512 ü ü
EB1710297-024 08-May-2017 00:00 1218_BH027_0.9-1.0_1... ü
EB1710297-025 08-May-2017 00:00 1218_BH027_0.5-0.75_... ü ü
EB1710297-026 08-May-2017 00:00 1218_BH027_7.8-8.0_1... ü ü
EB1710297-027 08-May-2017 00:00 1218_BH027_11.5-11.7... ü
EB1710297-028 09-May-2017 00:00 1218_BH026_0.6-0.75_... ü ü
EB1710297-029 09-May-2017 00:00 1218_BH026_1.4-1.5_1... ü
EB1710297-030 09-May-2017 00:00 1218_BH026_7.0-7.25_... ü ü
EB1710297-031 09-May-2017 00:00 1218_BH026_13.4-13.5... ü
EB1710297-032 09-May-2017 00:00 1218_QC104_170509 ü ü
EB1710297-036 09-May-2017 00:00 1218_SD013_0.0_170509 ü ü
EB1710297-037 10-May-2017 00:00 1218_BH023_0.6-0.75_... ü ü
Matrix: SOIL
Client sample IDLaboratory sample
ID
Client sampling
date / time
:Client GOLDER ASSOCIATES
Work Order : EB1710297 Amendment 03 of 4:Page
19-May-2017:Issue Date
(On H
old
) S
OIL
No a
na
lysi
s re
que
ste
d
SO
IL -
EA
05
5-1
03
Mo
istu
re C
onte
nt
SO
IL -
EP
23
1X
(so
lids)
PF
AS
- F
ull
Suite
(28 a
naly
tes)
EB1710297-038 10-May-2017 00:00 1218_BH023_1.9-2.0_1... ü
EB1710297-039 10-May-2017 00:00 1218_BH023_4.5-4.75_... ü
EB1710297-040 10-May-2017 00:00 1218_BH023_13.8-14.0... ü ü
EB1710297-041 10-May-2017 00:00 1218_BH023_16.8-17.0... ü
EB1710297-042 13-May-2017 00:00 1218_BH022_0.7-0.95_... ü ü
EB1710297-043 13-May-2017 00:00 1218_BH022_7.5-7.75_... ü
EB1710297-044 13-May-2017 00:00 1218_BH022_11.5-11.7... ü ü
EB1710297-045 13-May-2017 00:00 1218_BH022_16.75-17.... ü
EB1710297-046 13-May-2017 00:00 1218_BH022_22.0-22.2... ü
EB1710297-047 13-May-2017 00:00 1218_QC108_170513 ü ü
EB1710297-050 13-May-2017 00:00 1218_IDW01_170513 ü ü
EB1710297-051 13-May-2017 00:00 1218_IDW02_170513 ü ü
EB1710297-052 13-May-2017 00:00 1218_IDW03_170513 ü ü
(On H
old
) W
AT
ER
No a
naly
sis
request
ed
WA
TE
R -
EP
231X
-LL
PF
AS
- F
ull
Suite
Low
Leve
l (2
8 a
na
lyte
s)
EB1710297-001 15-May-2017 00:00 1218_MW026_S_170515 ü
EB1710297-002 15-May-2017 00:00 1218_MW027_S_170515 ü
EB1710297-003 15-May-2017 00:00 1218_MW022_S_170515 ü
EB1710297-004 15-May-2017 00:00 1218_MW023_S_170515 ü
EB1710297-005 15-May-2017 00:00 1218_MWO24_S_170515 ü
EB1710297-006 15-May-2017 00:00 1218_MW025_S_170515 ü
EB1710297-007 15-May-2017 00:00 1218_QC109_170515 ü
EB1710297-008 15-May-2017 00:00 1218_QC309_170515 ü
EB1710297-009 15-May-2017 00:00 1218_QC110_170515 ü
EB1710297-021 12-May-2017 00:00 1218_QC307_170511 ü
EB1710297-022 13-May-2017 00:00 1218_QC308_170512 ü
EB1710297-033 08-May-2017 00:00 1218_QC303_170508 ü
EB1710297-034 09-May-2017 00:00 1218_QC304_170509 ü
EB1710297-035 09-May-2017 00:00 1218_SW013_170509 ü
EB1710297-048 10-May-2017 00:00 1218_QC305_170510 ü
EB1710297-049 13-May-2017 00:00 1218_QC306_170511 ü
Matrix: WATER
Client sample IDLaboratory sample
ID
Client sampling
date / time
:Client GOLDER ASSOCIATES
Work Order : EB1710297 Amendment 04 of 4:Page
19-May-2017:Issue Date
Proactive Holding Time Report
Sample(s) have been received within the recommended holding times for the requested analysis.
Requested Deliverables
ACCOUNTS PAYABLE
- A4 - AU Tax Invoice (INV) Email [email protected]
u
DARCY SIMPSON
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
ERIN CORBY
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
FRAN MITCHELL
- *AU Certificate of Analysis - NATA (COA) Email [email protected]
- *AU Interpretive QC Report - DEFAULT (Anon QCI Rep) (QCI) Email [email protected]
- *AU QC Report - DEFAULT (Anon QC Rep) - NATA (QC) Email [email protected]
- A4 - AU Sample Receipt Notification - Environmental HT (SRN) Email [email protected]
- Chain of Custody (CoC) (COC) Email [email protected]
- EDI Format - ESDAT (ESDAT) Email [email protected]
True
Environmental
QA/QC Compliance Assessment to assist with Quality ReviewWork Order : EB1710297 Page : 1 of 9
:: LaboratoryClient Environmental Division BrisbaneGOLDER ASSOCIATES
:Contact MS FRAN MITCHELL Telephone : +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 19-May-2017
Site : ---- Issue Date : 26-May-2017
DARCY SIMPSON:Sampler No. of samples received : 52
:Order number 1669286 No. of samples analysed : 34
This report is automatically generated by the ALS LIMS through interpretation of the ALS Quality Control Report and several Quality Assurance parameters measured by ALS. This automated
reporting highlights any non-conformances, facilitates faster and more accurate data validation and is designed to assist internal expert and external Auditor review. Many components of this
report contribute to the overall DQO assessment and reporting for guideline compliance.
Brief method summaries and references are also provided to assist in traceability.
Summary of Outliers
Outliers : Quality Control Samples
This report highlights outliers flagged in the Quality Control (QC) Report.
l NO Method Blank value outliers occur.
l NO Duplicate outliers occur.
l NO Laboratory Control outliers occur.
l NO Matrix Spike outliers occur.
l For all regular sample matrices, NO surrogate recovery outliers occur.
Outliers : Analysis Holding Time Compliance
l Analysis Holding Time Outliers exist - please see following pages for full details.
Outliers : Frequency of Quality Control Samples
l NO Quality Control Sample Frequency Outliers exist.
R I G H T S O L U T I O N S | R I G H T P A R T N E R
2 of 9:Page
Work Order :
:Client
EB1710297
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Outliers : Analysis Holding Time Compliance
Matrix: SOIL
AnalysisExtraction / Preparation
Date analysedDate extractedContainer / Client Sample ID(s) Days
overdue
Days
overdue
Due for extraction Due for analysis
Method
EA055: Moisture Content
HDPE Soil Jar
22-May-2017----1218_BH027_0.5-0.75_170508, 1218_BH027_7.8-8.0_170508 23-May-2017---- ---- 1
Analysis Holding Time Compliance
Holding times for VOC in soils vary according to analytes of interest. Vinyl Chloride and Styrene holding time is 7 days; others 14 days. A recorded breach does not guarantee a breach for all VOC analytes and
should be verified in case the reported breach is a false positive or Vinyl Chloride and Styrene are not key analytes of interest/concern.
Holding time for leachate methods (e.g. TCLP) vary according to the analytes reported. Assessment compares the leach date with the shortest analyte holding time for the equivalent soil method. These are: organics
14 days, mercury 28 days & other metals 180 days. A recorded breach does not guarantee a breach for all non-volatile parameters.
If samples are identified below as having been analysed or extracted outside of recommended holding times, this should be taken into consideration when interpreting results.
This report summarizes extraction / preparation and analysis times and compares each with ALS recommended holding times (referencing USEPA SW 846, APHA, AS and NEPM) based on the sample container
provided. Dates reported represent first date of extraction or analysis and preclude subsequent dilutions and reruns. A listing of breaches (if any) is provided herein.
Matrix: SOIL Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EA055: Moisture Content
HDPE Soil Jar (EA055-103)
1218_BH027_0.5-0.75_170508, 1218_BH027_7.8-8.0_170508 22-May-2017---- 23-May-2017----08-May-2017 ---- ûHDPE Soil Jar (EA055-103)
1218_BH026_0.6-0.75_170509, 1218_BH026_7.0-7.25_170509,
1218_QC104_170509, 1218_SD013_0.0_170509
23-May-2017---- 23-May-2017----09-May-2017 ---- ü
HDPE Soil Jar (EA055-103)
1218_BH025_0.6-0.75170510, 1218_BH023_0.6-0.75_170510,
1218_BH023_13.8-14.0_170510
24-May-2017---- 23-May-2017----10-May-2017 ---- ü
HDPE Soil Jar (EA055-103)
1218_BH025_16.5-16.75170511 25-May-2017---- 23-May-2017----11-May-2017 ---- üHDPE Soil Jar (EA055-103)
1218_BH024_0.8-1.0_170512, 1218_BH024_8.5-8.75_170512,
1218_QC107_170512
26-May-2017---- 23-May-2017----12-May-2017 ---- ü
HDPE Soil Jar (EA055-103)
1218_BH022_0.7-0.95_170511, 1218_BH022_11.5-11.75_170511,
1218_QC108_170513, 1218_IDW01_170513,
1218_IDW02_170513, 1218_IDW03_170513
27-May-2017---- 23-May-2017----13-May-2017 ---- ü
3 of 9:Page
Work Order :
:Client
EB1710297
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Matrix: SOIL Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231A: Perfluoroalkyl Sulfonic Acids
HDPE Soil Jar (EP231X)
1218_BH027_0.5-0.75_170508, 1218_BH027_7.8-8.0_170508 04-Jul-201704-Nov-2017 25-May-201725-May-201708-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH026_0.6-0.75_170509, 1218_BH026_7.0-7.25_170509,
1218_QC104_170509, 1218_SD013_0.0_170509
04-Jul-201705-Nov-2017 25-May-201725-May-201709-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_0.6-0.75170510, 1218_BH023_0.6-0.75_170510,
1218_BH023_13.8-14.0_170510
04-Jul-201706-Nov-2017 25-May-201725-May-201710-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_16.5-16.75170511 04-Jul-201707-Nov-2017 25-May-201725-May-201711-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH024_0.8-1.0_170512, 1218_BH024_8.5-8.75_170512,
1218_QC107_170512
04-Jul-201708-Nov-2017 25-May-201725-May-201712-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH022_0.7-0.95_170511, 1218_BH022_11.5-11.75_170511,
1218_QC108_170513, 1218_IDW01_170513,
1218_IDW02_170513, 1218_IDW03_170513
04-Jul-201709-Nov-2017 25-May-201725-May-201713-May-2017 ü ü
EP231B: Perfluoroalkyl Carboxylic Acids
HDPE Soil Jar (EP231X)
1218_BH027_0.5-0.75_170508, 1218_BH027_7.8-8.0_170508 04-Jul-201704-Nov-2017 25-May-201725-May-201708-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH026_0.6-0.75_170509, 1218_BH026_7.0-7.25_170509,
1218_QC104_170509, 1218_SD013_0.0_170509
04-Jul-201705-Nov-2017 25-May-201725-May-201709-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_0.6-0.75170510, 1218_BH023_0.6-0.75_170510,
1218_BH023_13.8-14.0_170510
04-Jul-201706-Nov-2017 25-May-201725-May-201710-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_16.5-16.75170511 04-Jul-201707-Nov-2017 25-May-201725-May-201711-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH024_0.8-1.0_170512, 1218_BH024_8.5-8.75_170512,
1218_QC107_170512
04-Jul-201708-Nov-2017 25-May-201725-May-201712-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH022_0.7-0.95_170511, 1218_BH022_11.5-11.75_170511,
1218_QC108_170513, 1218_IDW01_170513,
1218_IDW02_170513, 1218_IDW03_170513
04-Jul-201709-Nov-2017 25-May-201725-May-201713-May-2017 ü ü
4 of 9:Page
Work Order :
:Client
EB1710297
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Matrix: SOIL Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231C: Perfluoroalkyl Sulfonamides
HDPE Soil Jar (EP231X)
1218_BH027_0.5-0.75_170508, 1218_BH027_7.8-8.0_170508 04-Jul-201704-Nov-2017 25-May-201725-May-201708-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH026_0.6-0.75_170509, 1218_BH026_7.0-7.25_170509,
1218_QC104_170509, 1218_SD013_0.0_170509
04-Jul-201705-Nov-2017 25-May-201725-May-201709-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_0.6-0.75170510, 1218_BH023_0.6-0.75_170510,
1218_BH023_13.8-14.0_170510
04-Jul-201706-Nov-2017 25-May-201725-May-201710-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_16.5-16.75170511 04-Jul-201707-Nov-2017 25-May-201725-May-201711-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH024_0.8-1.0_170512, 1218_BH024_8.5-8.75_170512,
1218_QC107_170512
04-Jul-201708-Nov-2017 25-May-201725-May-201712-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH022_0.7-0.95_170511, 1218_BH022_11.5-11.75_170511,
1218_QC108_170513, 1218_IDW01_170513,
1218_IDW02_170513, 1218_IDW03_170513
04-Jul-201709-Nov-2017 25-May-201725-May-201713-May-2017 ü ü
EP231D: (n:2) Fluorotelomer Sulfonic Acids
HDPE Soil Jar (EP231X)
1218_BH027_0.5-0.75_170508, 1218_BH027_7.8-8.0_170508 04-Jul-201704-Nov-2017 25-May-201725-May-201708-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH026_0.6-0.75_170509, 1218_BH026_7.0-7.25_170509,
1218_QC104_170509, 1218_SD013_0.0_170509
04-Jul-201705-Nov-2017 25-May-201725-May-201709-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_0.6-0.75170510, 1218_BH023_0.6-0.75_170510,
1218_BH023_13.8-14.0_170510
04-Jul-201706-Nov-2017 25-May-201725-May-201710-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_16.5-16.75170511 04-Jul-201707-Nov-2017 25-May-201725-May-201711-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH024_0.8-1.0_170512, 1218_BH024_8.5-8.75_170512,
1218_QC107_170512
04-Jul-201708-Nov-2017 25-May-201725-May-201712-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH022_0.7-0.95_170511, 1218_BH022_11.5-11.75_170511,
1218_QC108_170513, 1218_IDW01_170513,
1218_IDW02_170513, 1218_IDW03_170513
04-Jul-201709-Nov-2017 25-May-201725-May-201713-May-2017 ü ü
5 of 9:Page
Work Order :
:Client
EB1710297
GOLDER ASSOCIATES
1669283 Phase: 9202:Project
Matrix: SOIL Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231P: PFAS Sums
HDPE Soil Jar (EP231X)
1218_BH027_0.5-0.75_170508, 1218_BH027_7.8-8.0_170508 04-Jul-201704-Nov-2017 25-May-201725-May-201708-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH026_0.6-0.75_170509, 1218_BH026_7.0-7.25_170509,
1218_QC104_170509, 1218_SD013_0.0_170509
04-Jul-201705-Nov-2017 25-May-201725-May-201709-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_0.6-0.75170510, 1218_BH023_0.6-0.75_170510,
1218_BH023_13.8-14.0_170510
04-Jul-201706-Nov-2017 25-May-201725-May-201710-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH025_16.5-16.75170511 04-Jul-201707-Nov-2017 25-May-201725-May-201711-May-2017 ü üHDPE Soil Jar (EP231X)
1218_BH024_0.8-1.0_170512, 1218_BH024_8.5-8.75_170512,
1218_QC107_170512
04-Jul-201708-Nov-2017 25-May-201725-May-201712-May-2017 ü ü
HDPE Soil Jar (EP231X)
1218_BH022_0.7-0.95_170511, 1218_BH022_11.5-11.75_170511,
1218_QC108_170513, 1218_IDW01_170513,
1218_IDW02_170513, 1218_IDW03_170513
04-Jul-201709-Nov-2017 25-May-201725-May-201713-May-2017 ü ü
Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231A: Perfluoroalkyl Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_QC303_170508 04-Nov-201704-Nov-2017 24-May-201724-May-201708-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC304_170509, 1218_SW013_170509 05-Nov-201705-Nov-2017 24-May-201724-May-201709-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC305_170510 06-Nov-201706-Nov-2017 24-May-201724-May-201710-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC307_170511 08-Nov-201708-Nov-2017 24-May-201724-May-201712-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC308_170512, 1218_QC306_170511 09-Nov-201709-Nov-2017 24-May-201724-May-201713-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_MW026_S_170515, 1218_MW027_S_170515,
1218_MW022_S_170515, 1218_MW023_S_170515,
1218_MWO24_S_170515, 1218_MW025_S_170515,
1218_QC309_170515, 1218_QC110_170515
11-Nov-201711-Nov-2017 24-May-201724-May-201715-May-2017 ü ü
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Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231B: Perfluoroalkyl Carboxylic Acids
HDPE (no PTFE) (EP231X-LL)
1218_QC303_170508 04-Nov-201704-Nov-2017 24-May-201724-May-201708-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC304_170509, 1218_SW013_170509 05-Nov-201705-Nov-2017 24-May-201724-May-201709-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC305_170510 06-Nov-201706-Nov-2017 24-May-201724-May-201710-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC307_170511 08-Nov-201708-Nov-2017 24-May-201724-May-201712-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC308_170512, 1218_QC306_170511 09-Nov-201709-Nov-2017 24-May-201724-May-201713-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_MW026_S_170515, 1218_MW027_S_170515,
1218_MW022_S_170515, 1218_MW023_S_170515,
1218_MWO24_S_170515, 1218_MW025_S_170515,
1218_QC309_170515, 1218_QC110_170515
11-Nov-201711-Nov-2017 24-May-201724-May-201715-May-2017 ü ü
EP231C: Perfluoroalkyl Sulfonamides
HDPE (no PTFE) (EP231X-LL)
1218_QC303_170508 04-Nov-201704-Nov-2017 24-May-201724-May-201708-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC304_170509, 1218_SW013_170509 05-Nov-201705-Nov-2017 24-May-201724-May-201709-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC305_170510 06-Nov-201706-Nov-2017 24-May-201724-May-201710-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC307_170511 08-Nov-201708-Nov-2017 24-May-201724-May-201712-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC308_170512, 1218_QC306_170511 09-Nov-201709-Nov-2017 24-May-201724-May-201713-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_MW026_S_170515, 1218_MW027_S_170515,
1218_MW022_S_170515, 1218_MW023_S_170515,
1218_MWO24_S_170515, 1218_MW025_S_170515,
1218_QC309_170515, 1218_QC110_170515
11-Nov-201711-Nov-2017 24-May-201724-May-201715-May-2017 ü ü
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Matrix: WATER Evaluation: û = Holding time breach ; ü = Within holding time.
AnalysisExtraction / PreparationSample DateMethod
EvaluationDue for analysisDate analysedEvaluationDue for extractionDate extractedContainer / Client Sample ID(s)
EP231D: (n:2) Fluorotelomer Sulfonic Acids
HDPE (no PTFE) (EP231X-LL)
1218_QC303_170508 04-Nov-201704-Nov-2017 24-May-201724-May-201708-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC304_170509, 1218_SW013_170509 05-Nov-201705-Nov-2017 24-May-201724-May-201709-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC305_170510 06-Nov-201706-Nov-2017 24-May-201724-May-201710-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC307_170511 08-Nov-201708-Nov-2017 24-May-201724-May-201712-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC308_170512, 1218_QC306_170511 09-Nov-201709-Nov-2017 24-May-201724-May-201713-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_MW026_S_170515, 1218_MW027_S_170515,
1218_MW022_S_170515, 1218_MW023_S_170515,
1218_MWO24_S_170515, 1218_MW025_S_170515,
1218_QC309_170515, 1218_QC110_170515
11-Nov-201711-Nov-2017 24-May-201724-May-201715-May-2017 ü ü
EP231P: PFAS Sums
HDPE (no PTFE) (EP231X-LL)
1218_QC303_170508 04-Nov-201704-Nov-2017 24-May-201724-May-201708-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC304_170509, 1218_SW013_170509 05-Nov-201705-Nov-2017 24-May-201724-May-201709-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC305_170510 06-Nov-201706-Nov-2017 24-May-201724-May-201710-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC307_170511 08-Nov-201708-Nov-2017 24-May-201724-May-201712-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_QC308_170512, 1218_QC306_170511 09-Nov-201709-Nov-2017 24-May-201724-May-201713-May-2017 ü üHDPE (no PTFE) (EP231X-LL)
1218_MW026_S_170515, 1218_MW027_S_170515,
1218_MW022_S_170515, 1218_MW023_S_170515,
1218_MWO24_S_170515, 1218_MW025_S_170515,
1218_QC309_170515, 1218_QC110_170515
11-Nov-201711-Nov-2017 24-May-201724-May-201715-May-2017 ü ü
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Quality Control Parameter Frequency ComplianceThe following report summarises the frequency of laboratory QC samples analysed within the analytical lot(s) in which the submitted sample(s) was(were) processed. Actual rate should be greater than or equal to
the expected rate. A listing of breaches is provided in the Summary of Outliers.
Matrix: SOIL Evaluation: û = Quality Control frequency not within specification ; ü = Quality Control frequency within specification.
Quality Control SpecificationQuality Control Sample Type
ExpectedQC Regular Actual
Rate (%)Quality Control Sample Type CountEvaluationAnalytical Methods Method
Laboratory Duplicates (DUP)
NEPM 2013 B3 & ALS QC Standard 10.00 10.004 40 üMoisture Content EA055-103
NEPM 2013 B3 & ALS QC Standard 10.53 10.002 19 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Laboratory Control Samples (LCS)
NEPM 2013 B3 & ALS QC Standard 5.26 5.001 19 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Method Blanks (MB)
NEPM 2013 B3 & ALS QC Standard 5.26 5.001 19 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Matrix Spikes (MS)
NEPM 2013 B3 & ALS QC Standard 5.26 5.001 19 üPer- and Polyfluoroalkyl Substances (PFAS) by LCMSMS EP231X
Matrix: WATER Evaluation: û = Quality Control frequency not within specification ; ü = Quality Control frequency within specification.
Quality Control SpecificationQuality Control Sample Type
ExpectedQC Regular Actual
Rate (%)Quality Control Sample Type CountEvaluationAnalytical Methods Method
Laboratory Duplicates (DUP)
NEPM 2013 B3 & ALS QC Standard 13.33 10.002 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Laboratory Control Samples (LCS)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Method Blanks (MB)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
Matrix Spikes (MS)
NEPM 2013 B3 & ALS QC Standard 6.67 5.001 15 üPer- and Polyfluoroalkyl Substances (PFAS by LCMSMS EP231X-LL
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Brief Method SummariesThe analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the US EPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request. The following report provides brief descriptions of the analytical procedures employed for results reported in the
Certificate of Analysis. Sources from which ALS methods have been developed are provided within the Method Descriptions.
Analytical Methods Method DescriptionsMatrixMethod
In house: A gravimetric procedure based on weight loss over a 12 hour drying period at 103-105 degrees C.
This method is compliant with NEPM (2013) Schedule B(3) Section 7.1 and Table 1 (14 day holding time).
Moisture Content EA055-103 SOIL
In-House. A portion of soil is extracted with MTBE. The extract is taken to dryness, made up in mobile phase.
Analysis is by LC/MSMS, ESI Negative Mode using MRM. PFOS is quantified using a certified, traceable standard
consisting of linear and branched PFOS isomers.
Per- and Polyfluoroalkyl Substances
(PFAS) by LCMSMS
EP231X SOIL
In-house: Analysis of fresh and saline waters by solid phase extraction followed by and LC-Electrospray-MS-MS,
Negative Mode using MRM. PFOS is quantified using a certified, traceable standard consisting of linear and
branched PFOS isomers.
Per- and Polyfluoroalkyl Substances
(PFAS by LCMSMS
EP231X-LL WATER
Preparation Methods Method DescriptionsMatrixMethod
In houseSample Extraction for PFAS EP231-PR SOIL
In houseSPE preparation for LL and saline PFCs EP231-SPE WATER
0 0.00 True
Environmental
CERTIFICATE OF ANALYSISWork Order : Page : 1 of 17EB1710297
:: LaboratoryClient GOLDER ASSOCIATES Environmental Division Brisbane
: :ContactContact MS FRAN MITCHELL Matt Frost
:: AddressAddress 216 DRAPER STREET
CAIRNS QLD, AUSTRALIA 4870
2 Byth Street Stafford QLD Australia 4053
:Telephone +61 07 3721 5400 :Telephone +61-7-3243 7222
:Project 1669283 Phase: 9202 Date Samples Received : 19-May-2017 13:20
:Order number 1669286 Date Analysis Commenced : 23-May-2017
:C-O-C number ---- Issue Date : 26-May-2017 17:34
Sampler : DARCY SIMPSON
Site : ----
Quote number : EN/002/16 v2
52:No. of samples received
34:No. of samples analysed
This report supersedes any previous report(s) with this reference. Results apply to the sample(s) as submitted. This document shall not be reproduced, except in full.
This Certificate of Analysis contains the following information:
l General Comments
l Analytical Results
l Surrogate Control Limits
Additional information pertinent to this report will be found in the following separate attachments: Quality Control Report, QA/QC Compliance Assessment to assist with
Quality Review and Sample Receipt Notification.
SignatoriesThis document has been electronically signed by the authorized signatories below. Electronic signing is carried out in compliance with procedures specified in 21 CFR Part 11.
Signatories Accreditation CategoryPosition
Alex Rossi Organic Chemist Sydney Organics, Smithfield, NSW
Edwandy Fadjar Organic Coordinator Sydney Inorganics, Smithfield, NSW
R I G H T S O L U T I O N S | R I G H T P A R T N E R
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General Comments
The analytical procedures used by the Environmental Division have been developed from established internationally recognized procedures such as those published by the USEPA, APHA, AS and NEPM. In house
developed procedures are employed in the absence of documented standards or by client request.
Where moisture determination has been performed, results are reported on a dry weight basis.
Where a reported less than (<) result is higher than the LOR, this may be due to primary sample extract/digestate dilution and/or insufficient sample for analysis.
Where the LOR of a reported result differs from standard LOR, this may be due to high moisture content, insufficient sample (reduced weight employed) or matrix interference.
When no sampling time is provided, the sampling time will default 00:00 on the date of sampling. If no sampling date is provided, the sampling date will be assumed by the laboratory and displayed in brackets without a
time component.
Where a result is required to meet compliance limits the associated uncertainty must be considered. Refer to the ALS Contact for details.
CAS Number = CAS registry number from database maintained by Chemical Abstracts Services. The Chemical Abstracts Service is a division of the American Chemical Society.
LOR = Limit of reporting
^ = This result is computed from individual analyte detections at or above the level of reporting
ø = ALS is not NATA accredited for these tests.
~ = Indicates an estimated value.
Key :
PFAS analysis will be conducted by ALS Environmental, Sydney, NATA accreditation no. 825, Site No. 10911 (Micro site no. 14913).l
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Analytical Results
1218_QC107_1705121218_BH025_16.5-16.
75170511
1218_BH025_0.6-0.75
170510
1218_BH024_8.5-8.75
_170512
1218_BH024_0.8-1.0_
170512
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
12-May-2017 00:0011-May-2017 00:0010-May-2017 00:00[12-May-2017][12-May-2017]Client sampling date / time
EB1710297-023EB1710297-018EB1710297-015EB1710297-011EB1710297-010UnitLORCAS NumberCompound
Result Result Result Result Result
EA055: Moisture Content
12.0 8.7 9.0 19.5 8.7%1----Moisture Content (dried @ 103°C)
EP231A: Perfluoroalkyl Sulfonic Acids
<0.0002Perfluorobutane sulfonic acid
(PFBS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-73-5
<0.0002Perfluoropentane sulfonic acid
(PFPeS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-91-4
<0.0002Perfluorohexane sulfonic acid
(PFHxS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002355-46-4
<0.0002Perfluoroheptane sulfonic acid
(PFHpS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-92-8
<0.0002Perfluorooctane sulfonic acid
(PFOS)
<0.0002 0.0231 <0.0002 <0.0002mg/kg0.00021763-23-1
<0.0002Perfluorodecane sulfonic acid
(PFDS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.001Perfluorobutanoic acid (PFBA) <0.001 <0.001 <0.001 <0.001mg/kg0.001375-22-4
<0.0002Perfluoropentanoic acid (PFPeA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-90-3
<0.0002Perfluorohexanoic acid (PFHxA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-24-4
<0.0002Perfluoroheptanoic acid (PFHpA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-85-9
<0.0002Perfluorooctanoic acid (PFOA) <0.0002 0.0002 <0.0002 <0.0002mg/kg0.0002335-67-1
<0.0002Perfluorononanoic acid (PFNA) <0.0002 0.0011 <0.0002 <0.0002mg/kg0.0002375-95-1
<0.0002Perfluorodecanoic acid (PFDA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-76-2
<0.0002Perfluoroundecanoic acid
(PFUnDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022058-94-8
<0.0002Perfluorododecanoic acid
(PFDoDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-55-1
<0.0002Perfluorotridecanoic acid
(PFTrDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.000272629-94-8
<0.0005Perfluorotetradecanoic acid
(PFTeDA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.0002Perfluorooctane sulfonamide
(FOSA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002754-91-6
<0.0005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000531506-32-8
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Analytical Results
1218_QC107_1705121218_BH025_16.5-16.
75170511
1218_BH025_0.6-0.75
170510
1218_BH024_8.5-8.75
_170512
1218_BH024_0.8-1.0_
170512
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
12-May-2017 00:0011-May-2017 00:0010-May-2017 00:00[12-May-2017][12-May-2017]Client sampling date / time
EB1710297-023EB1710297-018EB1710297-015EB1710297-011EB1710297-010UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.0005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00054151-50-2
<0.0005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00052448-09-7
<0.0005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00051691-99-2
<0.0002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022355-31-9
<0.0002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.00054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005757124-72-4
<0.00056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000527619-97-2
<0.00058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000539108-34-4
<0.000510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005120226-60-0
EP231P: PFAS Sums
<0.0002 <0.0002 0.0244 <0.0002 <0.0002mg/kg0.0002----Sum of PFAS
<0.0002Sum of PFHxS and PFOS <0.0002 0.0231 <0.0002 <0.0002mg/kg0.0002355-46-4/1763-23-
1
<0.0002 <0.0002 0.0233 <0.0002 <0.0002mg/kg0.0002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
85.2 86.0 83.3 81.9 76.7%0.0002----13C4-PFOS
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Analytical Results
1218_QC104_1705091218_BH026_7.0-7.25
_170509
1218_BH026_0.6-0.75
_170509
1218_BH027_7.8-8.0_
170508
1218_BH027_0.5-0.75
_170508
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
09-May-2017 00:0009-May-2017 00:0009-May-2017 00:0008-May-2017 00:0008-May-2017 00:00Client sampling date / time
EB1710297-032EB1710297-030EB1710297-028EB1710297-026EB1710297-025UnitLORCAS NumberCompound
Result Result Result Result Result
EA055: Moisture Content
9.8 18.1 13.4 21.8 18.1%1----Moisture Content (dried @ 103°C)
EP231A: Perfluoroalkyl Sulfonic Acids
<0.0002Perfluorobutane sulfonic acid
(PFBS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-73-5
<0.0002Perfluoropentane sulfonic acid
(PFPeS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-91-4
<0.0002Perfluorohexane sulfonic acid
(PFHxS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002355-46-4
<0.0002Perfluoroheptane sulfonic acid
(PFHpS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-92-8
<0.0002Perfluorooctane sulfonic acid
(PFOS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00021763-23-1
<0.0002Perfluorodecane sulfonic acid
(PFDS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.001Perfluorobutanoic acid (PFBA) <0.001 <0.001 <0.001 <0.001mg/kg0.001375-22-4
<0.0002Perfluoropentanoic acid (PFPeA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-90-3
<0.0002Perfluorohexanoic acid (PFHxA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-24-4
<0.0002Perfluoroheptanoic acid (PFHpA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-85-9
<0.0002Perfluorooctanoic acid (PFOA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-67-1
<0.0002Perfluorononanoic acid (PFNA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-95-1
<0.0002Perfluorodecanoic acid (PFDA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-76-2
<0.0002Perfluoroundecanoic acid
(PFUnDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022058-94-8
<0.0002Perfluorododecanoic acid
(PFDoDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-55-1
<0.0002Perfluorotridecanoic acid
(PFTrDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.000272629-94-8
<0.0005Perfluorotetradecanoic acid
(PFTeDA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.0002Perfluorooctane sulfonamide
(FOSA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002754-91-6
<0.0005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000531506-32-8
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Analytical Results
1218_QC104_1705091218_BH026_7.0-7.25
_170509
1218_BH026_0.6-0.75
_170509
1218_BH027_7.8-8.0_
170508
1218_BH027_0.5-0.75
_170508
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
09-May-2017 00:0009-May-2017 00:0009-May-2017 00:0008-May-2017 00:0008-May-2017 00:00Client sampling date / time
EB1710297-032EB1710297-030EB1710297-028EB1710297-026EB1710297-025UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.0005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00054151-50-2
<0.0005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00052448-09-7
<0.0005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00051691-99-2
<0.0002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022355-31-9
<0.0002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.00054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005757124-72-4
<0.00056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000527619-97-2
<0.00058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000539108-34-4
<0.000510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005120226-60-0
EP231P: PFAS Sums
<0.0002 <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002----Sum of PFAS
<0.0002Sum of PFHxS and PFOS <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002355-46-4/1763-23-
1
<0.0002 <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
78.3 82.0 82.9 83.4 94.0%0.0002----13C4-PFOS
7 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_BH022_11.5-11.
75_170511
1218_BH022_0.7-0.95
_170511
1218_BH023_13.8-14.
0_170510
1218_BH023_0.6-0.75
_170510
1218_SD013_0.0_170
509
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
13-May-2017 00:0013-May-2017 00:0010-May-2017 00:0010-May-2017 00:0009-May-2017 00:00Client sampling date / time
EB1710297-044EB1710297-042EB1710297-040EB1710297-037EB1710297-036UnitLORCAS NumberCompound
Result Result Result Result Result
EA055: Moisture Content
52.7 12.6 20.4 10.5 12.1%1----Moisture Content (dried @ 103°C)
EP231A: Perfluoroalkyl Sulfonic Acids
<0.0002Perfluorobutane sulfonic acid
(PFBS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-73-5
<0.0002Perfluoropentane sulfonic acid
(PFPeS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-91-4
<0.0002Perfluorohexane sulfonic acid
(PFHxS)
0.0005 <0.0002 <0.0002 <0.0002mg/kg0.0002355-46-4
<0.0002Perfluoroheptane sulfonic acid
(PFHpS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-92-8
0.0002Perfluorooctane sulfonic acid
(PFOS)
<0.0002 <0.0002 0.0013 <0.0002mg/kg0.00021763-23-1
<0.0002Perfluorodecane sulfonic acid
(PFDS)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.001Perfluorobutanoic acid (PFBA) <0.001 <0.001 <0.001 <0.001mg/kg0.001375-22-4
<0.0002Perfluoropentanoic acid (PFPeA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022706-90-3
<0.0002Perfluorohexanoic acid (PFHxA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-24-4
<0.0002Perfluoroheptanoic acid (PFHpA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-85-9
<0.0002Perfluorooctanoic acid (PFOA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-67-1
<0.0002Perfluorononanoic acid (PFNA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002375-95-1
<0.0002Perfluorodecanoic acid (PFDA) <0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002335-76-2
<0.0002Perfluoroundecanoic acid
(PFUnDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022058-94-8
<0.0002Perfluorododecanoic acid
(PFDoDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002307-55-1
<0.0002Perfluorotridecanoic acid
(PFTrDA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.000272629-94-8
<0.0005Perfluorotetradecanoic acid
(PFTeDA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.0002Perfluorooctane sulfonamide
(FOSA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.0002754-91-6
<0.0005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000531506-32-8
8 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_BH022_11.5-11.
75_170511
1218_BH022_0.7-0.95
_170511
1218_BH023_13.8-14.
0_170510
1218_BH023_0.6-0.75
_170510
1218_SD013_0.0_170
509
Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
13-May-2017 00:0013-May-2017 00:0010-May-2017 00:0010-May-2017 00:0009-May-2017 00:00Client sampling date / time
EB1710297-044EB1710297-042EB1710297-040EB1710297-037EB1710297-036UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.0005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00054151-50-2
<0.0005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00052448-09-7
<0.0005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.00051691-99-2
<0.0002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022355-31-9
<0.0002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.0002 <0.0002 <0.0002 <0.0002mg/kg0.00022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.00054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005757124-72-4
<0.00056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000527619-97-2
<0.00058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.000539108-34-4
<0.000510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.0005 <0.0005 <0.0005 <0.0005mg/kg0.0005120226-60-0
EP231P: PFAS Sums
0.0002 0.0005 <0.0002 0.0013 <0.0002mg/kg0.0002----Sum of PFAS
0.0002Sum of PFHxS and PFOS 0.0005 <0.0002 0.0013 <0.0002mg/kg0.0002355-46-4/1763-23-
1
0.0002 0.0005 <0.0002 0.0013 <0.0002mg/kg0.0002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
95.2 91.4 80.3 83.0 78.9%0.0002----13C4-PFOS
9 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
----1218_IDW03_1705131218_IDW02_1705131218_IDW01_1705131218_QC108_170513Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
----13-May-2017 00:0013-May-2017 00:0013-May-2017 00:0013-May-2017 00:00Client sampling date / time
--------EB1710297-052EB1710297-051EB1710297-050EB1710297-047UnitLORCAS NumberCompound
Result Result Result Result ----
EA055: Moisture Content
12.0 7.6 8.5 8.4 ----%1----Moisture Content (dried @ 103°C)
EP231A: Perfluoroalkyl Sulfonic Acids
<0.0002Perfluorobutane sulfonic acid
(PFBS)
<0.0002 <0.0002 <0.0002 ----mg/kg0.0002375-73-5
<0.0002Perfluoropentane sulfonic acid
(PFPeS)
<0.0002 <0.0002 <0.0002 ----mg/kg0.00022706-91-4
<0.0002Perfluorohexane sulfonic acid
(PFHxS)
<0.0002 <0.0002 <0.0002 ----mg/kg0.0002355-46-4
<0.0002Perfluoroheptane sulfonic acid
(PFHpS)
<0.0002 <0.0002 <0.0002 ----mg/kg0.0002375-92-8
<0.0002Perfluorooctane sulfonic acid
(PFOS)
0.0004 0.0024 0.0020 ----mg/kg0.00021763-23-1
<0.0002Perfluorodecane sulfonic acid
(PFDS)
<0.0002 <0.0002 <0.0002 ----mg/kg0.0002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.001Perfluorobutanoic acid (PFBA) <0.001 <0.001 <0.001 ----mg/kg0.001375-22-4
<0.0002Perfluoropentanoic acid (PFPeA) <0.0002 <0.0002 <0.0002 ----mg/kg0.00022706-90-3
<0.0002Perfluorohexanoic acid (PFHxA) <0.0002 <0.0002 <0.0002 ----mg/kg0.0002307-24-4
<0.0002Perfluoroheptanoic acid (PFHpA) <0.0002 <0.0002 <0.0002 ----mg/kg0.0002375-85-9
<0.0002Perfluorooctanoic acid (PFOA) <0.0002 <0.0002 <0.0002 ----mg/kg0.0002335-67-1
<0.0002Perfluorononanoic acid (PFNA) <0.0002 <0.0002 <0.0002 ----mg/kg0.0002375-95-1
<0.0002Perfluorodecanoic acid (PFDA) <0.0002 <0.0002 <0.0002 ----mg/kg0.0002335-76-2
<0.0002Perfluoroundecanoic acid
(PFUnDA)
<0.0002 <0.0002 <0.0002 ----mg/kg0.00022058-94-8
<0.0002Perfluorododecanoic acid
(PFDoDA)
<0.0002 <0.0002 <0.0002 ----mg/kg0.0002307-55-1
<0.0002Perfluorotridecanoic acid
(PFTrDA)
<0.0002 <0.0002 <0.0002 ----mg/kg0.000272629-94-8
<0.0005Perfluorotetradecanoic acid
(PFTeDA)
<0.0005 <0.0005 <0.0005 ----mg/kg0.0005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.0002Perfluorooctane sulfonamide
(FOSA)
<0.0002 <0.0002 <0.0002 ----mg/kg0.0002754-91-6
<0.0005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.0005 <0.0005 <0.0005 ----mg/kg0.000531506-32-8
10 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
----1218_IDW03_1705131218_IDW02_1705131218_IDW01_1705131218_QC108_170513Client sample IDSub-Matrix: SOIL
(Matrix: SOIL)
----13-May-2017 00:0013-May-2017 00:0013-May-2017 00:0013-May-2017 00:00Client sampling date / time
--------EB1710297-052EB1710297-051EB1710297-050EB1710297-047UnitLORCAS NumberCompound
Result Result Result Result ----
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.0005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.0005 <0.0005 <0.0005 ----mg/kg0.00054151-50-2
<0.0005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.0005 <0.0005 <0.0005 ----mg/kg0.00052448-09-7
<0.0005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.0005 <0.0005 <0.0005 ----mg/kg0.00051691-99-2
<0.0002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.0002 <0.0002 <0.0002 ----mg/kg0.00022355-31-9
<0.0002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.0002 <0.0002 <0.0002 ----mg/kg0.00022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.00054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.0005 <0.0005 <0.0005 ----mg/kg0.0005757124-72-4
<0.00056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.0005 <0.0005 <0.0005 ----mg/kg0.000527619-97-2
<0.00058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.0005 <0.0005 <0.0005 ----mg/kg0.000539108-34-4
<0.000510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.0005 <0.0005 <0.0005 ----mg/kg0.0005120226-60-0
EP231P: PFAS Sums
<0.0002 0.0004 0.0024 0.0020 ----mg/kg0.0002----Sum of PFAS
<0.0002Sum of PFHxS and PFOS 0.0004 0.0024 0.0020 ----mg/kg0.0002355-46-4/1763-23-
1
<0.0002 0.0004 0.0024 0.0020 ----mg/kg0.0002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
70.4 76.9 75.2 77.2 ----%0.0002----13C4-PFOS
11 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_MWO24_S_170
515
1218_MW023_S_1705
15
1218_MW022_S_1705
15
1218_MW027_S_1705
15
1218_MW026_S_1705
15
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
15-May-2017 00:0015-May-2017 00:0015-May-2017 00:0015-May-2017 00:0015-May-2017 00:00Client sampling date / time
EB1710297-005EB1710297-004EB1710297-003EB1710297-002EB1710297-001UnitLORCAS NumberCompound
Result Result Result Result Result
EP231A: Perfluoroalkyl Sulfonic Acids
<0.002Perfluorobutane sulfonic acid
(PFBS)
<0.002 0.003 <0.002 0.020µg/L0.002375-73-5
<0.002Perfluoropentane sulfonic acid
(PFPeS)
<0.002 0.002 <0.002 0.011µg/L0.0022706-91-4
<0.002Perfluorohexane sulfonic acid
(PFHxS)
<0.002 0.008 <0.002 0.037µg/L0.002355-46-4
<0.002Perfluoroheptane sulfonic acid
(PFHpS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-92-8
<0.002Perfluorooctane sulfonic acid
(PFOS)
0.003 0.008 <0.002 0.023µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
<0.002 <0.002 <0.002 <0.002µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) <0.01 <0.01 <0.01 <0.01µg/L0.01375-22-4
<0.002Perfluoropentanoic acid (PFPeA) <0.002 0.003 <0.002 0.019µg/L0.0022706-90-3
<0.002Perfluorohexanoic acid (PFHxA) <0.002 0.008 <0.002 0.018µg/L0.002307-24-4
<0.002Perfluoroheptanoic acid (PFHpA) <0.002 <0.002 <0.002 0.006µg/L0.002375-85-9
<0.002Perfluorooctanoic acid (PFOA) <0.002 0.002 <0.002 0.002µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
<0.002 <0.002 <0.002 <0.002µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
<0.002 <0.002 <0.002 <0.002µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
<0.005 <0.005 <0.005 <0.005µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
<0.002 <0.002 <0.002 <0.002µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.0054151-50-2
12 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_MWO24_S_170
515
1218_MW023_S_1705
15
1218_MW022_S_1705
15
1218_MW027_S_1705
15
1218_MW026_S_1705
15
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
15-May-2017 00:0015-May-2017 00:0015-May-2017 00:0015-May-2017 00:0015-May-2017 00:00Client sampling date / time
EB1710297-005EB1710297-004EB1710297-003EB1710297-002EB1710297-001UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005757124-72-4
<0.0056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.005 <0.005 <0.005 0.046µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005120226-60-0
EP231P: PFAS Sums
<0.002 0.003 0.034 <0.002 0.182µg/L0.002----Sum of PFAS
<0.002Sum of PFHxS and PFOS 0.003 0.016 <0.002 0.060µg/L0.002355-46-4/1763-23-
1
<0.002 <0.002 0.026 <0.002 0.159µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
110 107 109 106 108%0.002----13C4-PFOS
13 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_QC308_1705121218_QC307_1705111218_QC110_1705151218_QC309_1705151218_MW025_S_1705
15
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
13-May-2017 00:0012-May-2017 00:0015-May-2017 00:0015-May-2017 00:0015-May-2017 00:00Client sampling date / time
EB1710297-022EB1710297-021EB1710297-009EB1710297-008EB1710297-006UnitLORCAS NumberCompound
Result Result Result Result Result
EP231A: Perfluoroalkyl Sulfonic Acids
0.026Perfluorobutane sulfonic acid
(PFBS)
<0.002 0.003 <0.002 <0.002µg/L0.002375-73-5
0.020Perfluoropentane sulfonic acid
(PFPeS)
<0.002 0.002 <0.002 <0.002µg/L0.0022706-91-4
0.106Perfluorohexane sulfonic acid
(PFHxS)
<0.002 0.009 <0.002 <0.002µg/L0.002355-46-4
0.007Perfluoroheptane sulfonic acid
(PFHpS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-92-8
0.073Perfluorooctane sulfonic acid
(PFOS)
0.003 0.009 <0.002 <0.002µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
<0.002 <0.002 <0.002 <0.002µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) <0.01 <0.01 <0.01 <0.01µg/L0.01375-22-4
0.028Perfluoropentanoic acid (PFPeA) <0.002 0.002 <0.002 <0.002µg/L0.0022706-90-3
0.052Perfluorohexanoic acid (PFHxA) <0.002 0.009 <0.002 <0.002µg/L0.002307-24-4
0.017Perfluoroheptanoic acid (PFHpA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-85-9
0.023Perfluorooctanoic acid (PFOA) <0.002 0.002 <0.002 <0.002µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
<0.002 <0.002 <0.002 <0.002µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
<0.002 <0.002 <0.002 <0.002µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
<0.005 <0.005 <0.005 <0.005µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
<0.002 <0.002 <0.002 <0.002µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.0054151-50-2
14 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_QC308_1705121218_QC307_1705111218_QC110_1705151218_QC309_1705151218_MW025_S_1705
15
Client sample IDSub-Matrix: WATER
(Matrix: WATER)
13-May-2017 00:0012-May-2017 00:0015-May-2017 00:0015-May-2017 00:0015-May-2017 00:00Client sampling date / time
EB1710297-022EB1710297-021EB1710297-009EB1710297-008EB1710297-006UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005757124-72-4
0.0226:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005120226-60-0
EP231P: PFAS Sums
0.374 0.003 0.036 <0.002 <0.002µg/L0.002----Sum of PFAS
0.179Sum of PFHxS and PFOS 0.003 0.018 <0.002 <0.002µg/L0.002355-46-4/1763-23-
1
0.294 <0.002 0.027 <0.002 <0.002µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
110 107 102 108 105%0.002----13C4-PFOS
15 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_QC306_1705111218_QC305_1705101218_SW013_1705091218_QC304_1705091218_QC303_170508Client sample IDSub-Matrix: WATER
(Matrix: WATER)
13-May-2017 00:0010-May-2017 00:0009-May-2017 00:0009-May-2017 00:0008-May-2017 00:00Client sampling date / time
EB1710297-049EB1710297-048EB1710297-035EB1710297-034EB1710297-033UnitLORCAS NumberCompound
Result Result Result Result Result
EP231A: Perfluoroalkyl Sulfonic Acids
<0.002Perfluorobutane sulfonic acid
(PFBS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-73-5
<0.002Perfluoropentane sulfonic acid
(PFPeS)
<0.002 <0.002 <0.002 <0.002µg/L0.0022706-91-4
<0.002Perfluorohexane sulfonic acid
(PFHxS)
<0.002 <0.002 <0.002 <0.002µg/L0.002355-46-4
<0.002Perfluoroheptane sulfonic acid
(PFHpS)
<0.002 <0.002 <0.002 <0.002µg/L0.002375-92-8
<0.002Perfluorooctane sulfonic acid
(PFOS)
<0.002 0.003 0.003 <0.002µg/L0.0021763-23-1
<0.002Perfluorodecane sulfonic acid
(PFDS)
<0.002 <0.002 <0.002 <0.002µg/L0.002335-77-3
EP231B: Perfluoroalkyl Carboxylic Acids
<0.01Perfluorobutanoic acid (PFBA) <0.01 <0.01 <0.01 <0.01µg/L0.01375-22-4
<0.002Perfluoropentanoic acid (PFPeA) <0.002 <0.002 <0.002 <0.002µg/L0.0022706-90-3
<0.002Perfluorohexanoic acid (PFHxA) <0.002 <0.002 <0.002 <0.002µg/L0.002307-24-4
<0.002Perfluoroheptanoic acid (PFHpA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-85-9
<0.002Perfluorooctanoic acid (PFOA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-67-1
<0.002Perfluorononanoic acid (PFNA) <0.002 <0.002 <0.002 <0.002µg/L0.002375-95-1
<0.002Perfluorodecanoic acid (PFDA) <0.002 <0.002 <0.002 <0.002µg/L0.002335-76-2
<0.002Perfluoroundecanoic acid
(PFUnDA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022058-94-8
<0.002Perfluorododecanoic acid
(PFDoDA)
<0.002 <0.002 <0.002 <0.002µg/L0.002307-55-1
<0.002Perfluorotridecanoic acid
(PFTrDA)
<0.002 <0.002 <0.002 <0.002µg/L0.00272629-94-8
<0.005Perfluorotetradecanoic acid
(PFTeDA)
<0.005 <0.005 <0.005 <0.005µg/L0.005376-06-7
EP231C: Perfluoroalkyl Sulfonamides
<0.002Perfluorooctane sulfonamide
(FOSA)
<0.002 <0.002 <0.002 <0.002µg/L0.002754-91-6
<0.005N-Methyl perfluorooctane
sulfonamide (MeFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.00531506-32-8
<0.005N-Ethyl perfluorooctane
sulfonamide (EtFOSA)
<0.005 <0.005 <0.005 <0.005µg/L0.0054151-50-2
16 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Analytical Results
1218_QC306_1705111218_QC305_1705101218_SW013_1705091218_QC304_1705091218_QC303_170508Client sample IDSub-Matrix: WATER
(Matrix: WATER)
13-May-2017 00:0010-May-2017 00:0009-May-2017 00:0009-May-2017 00:0008-May-2017 00:00Client sampling date / time
EB1710297-049EB1710297-048EB1710297-035EB1710297-034EB1710297-033UnitLORCAS NumberCompound
Result Result Result Result Result
EP231C: Perfluoroalkyl Sulfonamides - Continued
<0.005N-Methyl perfluorooctane
sulfonamidoethanol (MeFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0052448-09-7
<0.005N-Ethyl perfluorooctane
sulfonamidoethanol (EtFOSE)
<0.005 <0.005 <0.005 <0.005µg/L0.0051691-99-2
<0.002N-Methyl perfluorooctane
sulfonamidoacetic acid
(MeFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022355-31-9
<0.002N-Ethyl perfluorooctane
sulfonamidoacetic acid
(EtFOSAA)
<0.002 <0.002 <0.002 <0.002µg/L0.0022991-50-6
EP231D: (n:2) Fluorotelomer Sulfonic Acids
<0.0054:2 Fluorotelomer sulfonic acid
(4:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005757124-72-4
<0.0056:2 Fluorotelomer sulfonic acid
(6:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00527619-97-2
<0.0058:2 Fluorotelomer sulfonic acid
(8:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.00539108-34-4
<0.00510:2 Fluorotelomer sulfonic acid
(10:2 FTS)
<0.005 <0.005 <0.005 <0.005µg/L0.005120226-60-0
EP231P: PFAS Sums
<0.002 <0.002 0.003 0.003 <0.002µg/L0.002----Sum of PFAS
<0.002Sum of PFHxS and PFOS <0.002 0.003 0.003 <0.002µg/L0.002355-46-4/1763-23-
1
<0.002 <0.002 <0.002 <0.002 <0.002µg/L0.002----Sum of PFAS (WA DER List)
EP231S: PFAS Surrogate
106 109 107 107 105%0.002----13C4-PFOS
17 of 17:Page
Work Order :
:Client
EB1710297
1669283 Phase: 9202:Project
GOLDER ASSOCIATES
Surrogate Control Limits
Recovery Limits (%)Sub-Matrix: SOIL
Compound CAS Number Low High
EP231S: PFAS Surrogate
13C4-PFOS ---- 70 130
Recovery Limits (%)Sub-Matrix: WATER
Compound CAS Number Low High
EP231S: PFAS Surrogate
13C4-PFOS ---- 70 120
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX I Well Survey Report
Surveyor Rob Cross
Date of Survey 17/05/2017
Equipment RTK GPS
Level Derived from Auspos
Well Name Easting (MGA) Northing (MGA) Ground RL (AHD) Measurement from Grnd to top of Pipe (mm) Top of Pipe RL (AHD)
MW022 617529.324 8604009.515 44.455 -0.158 44.297
MW023 617970.553 8603882.900 44.500 -0.145 44.355
MW024 616647.230 8604067.650 43.964 -0.156 43.808
MW025 616943.909 8604111.031 43.920 -0.145 43.775
MW026 616721.154 8601407.517 39.325 -0.127 39.198
MW027 614820.754 8604848.414 22.301 0.690 22.991
RAAFSGR10 616747.749 8603605.201 41.635 -0.110 41.525
RAAFSGR14 617686.989 8603492.971 38.487 0.525 39.012
RAAFSGR15 617693.927 8603487.547 38.339
RAAFSGR16 617701.114 8603494.461 38.619 -0.120 38.499
RAAFSGR17 617706.309 8603502.838 38.868 -0.110 38.758
RAAFSGR18 617736.029 8602772.874 44.366 -0.120 44.246
RAAFSGR19 617731.304 8602763.232 44.294 -0.080 44.214
RAAFSGR20 617737.395 8602746.547 44.381 -0.090 44.291
RAAFSGR21 617749.594 8602731.108 44.719
W001PRE 617790.877 8602033.796
W002POST 617760.448 8602070.245
RL Not Required
RL Not Required
Could Not Open Gatic Lid
Could Not Open Gatic Lid
A1AMENDMENTS
REV NOTES:DESCRIPTION DATE APPROVED DRAWN BY:
CHECKED BY:
APPROVED BY:
DWG No:CLIENT:
NM
RC
RC
GOLDER ASSOC PTY LTD 2017-0085-A
ASCONSTRUCTED SURVEY
2017-0085 / 001WEIPA
DEFENCE BASE WELL POSITIONS
SHEET 1 of 1
SCI QUAL
INTERNATIONAL
QUALITY APPROVED
AS/NZS ISO 9001:2008
REGN. Number 3584
QUA
L
I
T
Y
S
Y
S
T
E
MS
AP
P
R
O
V
E
D
JOB NO:2017-0085
DATE:02/06/2017
SURVEYOR:RC
Data file:2017-0085-A
4002000
Meters
1:7500
200
613900.000 614600.000 615300.000 616000.000 616700.000 617400.000 618100.000 618800.000 619500.000
86
01
60
0.0
00
8602
300
.00
08
60
300
0.00
08
60
37
00
.0
00
86
04
40
0.0
00
86
01
60
0.0
00
8602
300
.00
08
60
300
0.00
08
60
37
00
.0
00
86
04
40
0.0
00
A CREATED 02/06/17 RC
- Coordinate System is MGA Zone 54
- Height Datum is AHD
- Survey Control based on AUSPOS observations.
- Information contained herein is true as per date of survey
PSI - RAAF BASE SCHERGER QLD (1218)
6 October 2017 Report No. 1669283-003-R-Rev2
APPENDIX J Report Limitations
IMPORTANT INFORMATION RELATING TO THIS REPORT
The document (“Report”) to which this page is attached and which this page forms a part of, has been issued by Golder Associates Pty Ltd (“Golder”) subject to the important limitations and other qualifications set out below.
This Report constitutes or is part of services (“Services”) provided by Golder to its client (“Client”) under and subject to a contract between Golder and its Client (“Contract”). The contents of this page are not intended to and do not alter Golder’s obligations (including any limits on those obligations) to its Client under the Contract.
This Report is provided for use solely by Golder’s Client and persons acting on the Client’s behalf, such as its professional advisers. Golder is responsible only to its Client for this Report. Golder has no responsibility to any other person who relies or makes decisions based upon this Report or who makes any other use of this Report. Golder accepts no responsibility for any loss or damage suffered by any person other than its Client as a result of any reliance upon any part of this Report, decisions made based upon this Report or any other use of it.
This Report has been prepared in the context of the circumstances and purposes referred to in, or derived from, the Contract and Golder accepts no responsibility for use of the Report, in whole or in part, in any other context or circumstance or for any other purpose.
The scope of Golder’s Services and the period of time they relate to are determined by the Contract and are subject to restrictions and limitations set out in the Contract. If a service or other work is not expressly referred to in this Report, do not assume that it has been provided or performed. If a matter is not addressed in this Report, do not assume that any determination has been made by Golder in regards to it.
At any location relevant to the Services conditions may exist which were not detected by Golder, in particular due to the specific scope of the investigation Golder has been engaged to undertake. Conditions can only be verified at the exact location of any tests undertaken. Variations in conditions may occur between tested locations and there may be conditions which have not been revealed by the investigation and which have not therefore been taken into account in this Report.
Golder accepts no responsibility for and makes no representation as to the accuracy or completeness of the information provided to it by or on behalf of the Client or sourced from any third party. Golder has assumed that such information is correct unless otherwise stated and no responsibility is accepted by Golder for incomplete or inaccurate data supplied by its Client or any other person for whom Golder is not responsible. Golder has not taken account of matters that may have existed when the Report was prepared but which were only later disclosed to Golder.
Having regard to the matters referred to in the previous paragraphs on this page in particular, carrying out the Services has allowed Golder to form no more than an opinion as to the actual conditions at any relevant location. That opinion is necessarily constrained by the extent of the information collected by Golder or otherwise made available to Golder. Further, the passage of time may affect the accuracy, applicability or usefulness of the opinions, assessments or other information in this Report. This Report is based upon the information and other circumstances that existed and were known to Golder when the Services were performed and this Report was prepared. Golder has not considered the effect of any possible future developments including physical changes to any relevant location or changes to any laws or regulations relevant to such location.
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By date, or revision, the Report supersedes any prior report or other document issued by Golder dealing with any matter that is addressed in the Report.
Any uncertainty as to the extent to which this Report can be used or relied upon in any respect should be referred to Golder for clarification.
GAP Form No. LEG04RL2July 2015 1/1
Golder Associates Pty Ltd
147 Coronation Drive
Milton, Queensland 4064
Australia
T: +61 7 3721 5400
Caption Text