Soils and Groundwater Baseline Screening Assessment & Baseline Report ESB … · 2019. 5. 28. · 13. ESB Site Drainage Testing Completion Report 2017 Project at ESB West Offaly Power,

1

Soils and Groundwater Baseline Screening Assessment

& Baseline Report

ESB West Offaly Power Station

Document No.: QS-000139-01-R460-018

Date: 05/04/2019

Engineering and Major Projects, One Dublin Airport Central, Dublin Airport, Cloghran, Co. Dublin,

K67 XF72, Ireland.

Phone +353 (0)1 703 8000

www.esb.ie

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33

http://www.esbi.ie/

2

File Reference:

Client/Recipient: ESB West Offaly Power Station

Project Title: IE Licence Review

Report Type: Soils and Groundwater Baseline Report

Report No. QS-000139-01-R460-018

Revision No. 0

Prepared by: Oonagh Duffy Date: 04/12/2018

Title: Senior Environmental Consultant

Verified by: Anne Marie Casey Date: 08/01/2019

Title: Senior Environmental Specialist

Approved by: Paddy Kavanagh Date: 28/04/2019

Title: Planning and Environmental

Team Manager

File

Copyright © ESB

All rights reserved. No part of this work may be modified, reproduced or copied in any form or by any means - graphic, electronic or mechanical, including photocopying, recording, taping or used for any purpose other than its designated purpose, without the written permission of ESB.

Template Used: T-020-017-Engineering and Major Projects Report Template

Change History of Report:

Date New revision Author Summary of Change

Table of Contents

1. Introduction .................................................................................................................... 6

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33

ESB West Offaly Power Station – Soils and Groundwater Baseline Assessment & Report

3

2. Methodology .................................................................................................................. 6

3. Previous Reports ........................................................................................................... 7

4. Preparing the Report ...................................................................................................... 9

5. Stage 1: Identifying the hazardous substances that are currently used, produced or

released at the installation .................................................................................................. 12

5.1 Guidance Requirements ....................................................................................... 12

5.2 Facility Details ....................................................................................................... 12

5.3 Substances used and generated at the Station & ADF ......................................... 12

6. Stage 2: Identifying the relevant hazardous substances............................................... 15


6.2 Identified Hazardous Substances .......................................................................... 15

7. Stage 3: Assessment of Potential Pollution Risk .......................................................... 16


7.2 Chemical Storage, Handling & Management......................................................... 16

The following storage and handling condition is stipulated under the IE Licence: ............ 16

7.3 Leachate from the ADF ......................................................................................... 17

7.4 Operational Discharges ........................................................................................ 18

7.5 Stage 3 Summary ................................................................................................. 21

8. Stage 4: Site History .................................................................................................... 22


8.2 Site History and Overview ..................................................................................... 22

8.2.1 Ash Disposal Facility ......................................................................................... 23

8.3 Exit Audit of the former ESB Power Station at Shannonbridge .............................. 24

8.4 WOP EIS 2001 ..................................................................................................... 24

8.5 Site Infrastructure.................................................................................................. 26

8.6 Incident History ..................................................................................................... 26

9. Stage 5: Environmental Setting .................................................................................... 27


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


4

9.2 Topography........................................................................................................... 27

9.3 Geology and Hydrogeology ................................................................................... 27

9.4 Hydrology ............................................................................................................. 29

9.5 Surrounding land use ............................................................................................ 29

9.6 Natural Habitats .................................................................................................... 30

9.7 Conceptual Site Model .......................................................................................... 30

10. Stage 6: Site Characterisation ...................................................................................... 32


10.2 Summary of Groundwater Quality, AECOM Risk Screening and Technical

Assessment, 2015 ........................................................................................................... 32

10.3 ESB 2017 Site Investigation Soil Analytical Results .............................................. 36

10.3.1 ESB 2017 SI Groundwater Monitoring Results .................................................. 38

10.4 Groundwater Monitoring Result 2014 -2017- AER Review .................................... 41

10.4.1 Station – PS - GW1 ........................................................................................... 43

10.4.2 Station – PS - GW2 ........................................................................................... 46

10.4.3 ADF - GW3 ........................................................................................................ 50

10.4.4 ADF- GW4 ......................................................................................................... 53

10.4.5 ADF - GW5 ........................................................................................................ 56

10.4.6 ADF - GW6 ........................................................................................................ 59

10.5 Summary of Soil Site Characteristics .................................................................... 62

10.6 Summary of Ground Water Site Characteristics .................................................... 62

11. Stage 7: Site investigation ............................................................................................ 67


11.2 Requirement for Site investigation ........................................................................ 67

12. Stage 8- Baseline Report ............................................................................................. 68

References ......................................................................................................................... 69

Appendix 1: Total Petroleum Hydrocarbons (TPH) Breakdown ........................................... 71

Appendix 2: CSM graphical Representation ........................................................................ 77

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


5

Appendix 3 Soil Analytical Results ...................................................................................... 80

Appendix 4.Soil Laboratory Results .................................................................................... 92

Appendix 5 Groundwater Analytical Results ...................................................................... 181

Appendix 6.Groundwater Laboratory Results .................................................................... 185

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


6

1. Introduction

West Offaly Power (WOP) station is an ESB peat fired station which has been commercially

operational since 2004. The WOP station has one unit, consisting of a boiler, turbine and

auxiliary plant, with an electricity generating capacity of 150MWe. The boiler operates on

peat with gas oil used for start-up. It is scheduled to burn approximately 1,250,000 energy

tonnes of peat each year.

The WOP station is applying to the Environmental Protection Agency (EPA) for a review of

its existing Industrial Emissions (IE) Licence (Licence no. P0611-02), see Attachment-1-1-

Reason for Licence Review. As part of the IE Licence review application, it is necessary to

prepare a Baseline Assessment and Report detailing the findings for submission to the EPA.

The objective of this report is to present the findings of this Baseline Assessment in relation

to soils and groundwater at the WOP site including its associated Ash Disposal Facility

(ADF).

2. Methodology

This report complies with the requirements of Article 22(2) of Directive 2010/75/EU, the

Industrial emissions Directive (IED), which states:

‘Where the activity involves the use, production or release of relevant hazardous

substances and having regard to the possibility of soil and groundwater

contamination at the site of the installation, the operator shall prepare and submit to

the competent authority a baseline report before starting operation of an installation

or before a permit for an installation is updated for the first time after 7 January 2013.

The baseline report shall contain the information necessary to determine the state of

soil and groundwater contamination so as to make a quantified comparison with the

state upon definitive cessation of activities provided for under paragraph 3.’

In addition, Article 22(2) of the IED specifies that a baseline report should contain the

following:

‘information on the present use and, where available, on past uses of the site; and

where available, existing information on soil and groundwater measurements that

reflect the state at the time the report is drawn up or, alternatively, new soil and

groundwater measurements having regard to the possibility of soil and groundwater

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


7

contamination by those hazardous substances to be used, produced or released by

the installation concerned.’

Consideration has also been given to the communication from the European Commission

(EC) namely the EC Guidance Concerning Baseline Reports1 under Article 22(2) of Directive

2010/75/EU on Industrial Emissions during the Compilation of this report.

In line with the commission guidance, there are 8 stages required in determining if a baseline

report is required and to produce the baseline report itself. These stages are as follows:

Stages 1-3: Screening Stages to decide whether a baseline report is required;

Stages 4-7: To determine how a baseline report has to be prepared; and

Stages 8: To determine the content of the report.

3. Previous Reports

A number of historical reports were reviewed during the compilation of this baseline soil and

groundwater assessment as follows:

1. West Offaly Power Industrial Emissions Licence (Licence P0611-02), Annual

Environmental Reports 2014, 2015, 2016 and 2017.

2. Shannonbridge New Peat Power Station Project Environmental Impact Statement

(EIS), Volume 1(ESB, February 2001).

3. West Offaly Power Environmental Liabilities Risk Assessment (ESB, 2016).

4. West Offaly Power Decommissioning Management Plan (DMP) and Closure,

Restoration and Aftercare Management Plan (CRAMP) (ESB, 2016)

5. ESB West Offaly Power Risk Screening and Technical Assessment (AECOM, August,

2015).

6. ESB West Offaly Power Further Environmental Assessment 2015 (AECOM,

November, 2015).

7. SEW Proposal for Permanent Capping Works for Cell No.1, No.2, No.3 and No. 4 at

West Offaly Power Ash Disposal Facility, completed by Bord Na Mona (2014-2016)

1 COMMUNICATION FROM THE COMMISSION; European Commission Guidance concerning

baseline reports under Article 22(2) of Directive 2010/75/EU on industrial emissions 2014/C

136/03

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


8

8. SEW Proposal for Construction of Cell No.5 at West Offaly Power Ash Disposal

Facility, completed by Bord Na Mona (April, 2016)

9. Operational Plan for West Offaly Ash Disposal Facility, prepared by Bord Na Mona

(April, 2015)

10. Shannonbridge Generating Station Environmental Site Investigation: Site

Characterisation Report, prepared by ESBI (September, 1995)

11. ESB Shannonbridge Environmental Exit Audit – Ash Ponds (related to the former ESB

Power Generating Station, Shannonbridge, Co. Offaly) (ESB, 2010).

12. West Offaly Power Station and the Ash Disposal Facility – Site Investigation: Factual

Report and Interpretative Report (Causeway Geotech, 2017)

13. ESB Site Drainage Testing Completion Report 2017 Project at ESB West Offaly

Power, Shannonbridge, Co. Offaly & ESB Lough Ree Power, Lanesborough, Co.

Longford (ESB, 2017).

In 2015, as required under IE Licence Condition 6.14.3, a Risk Screening and Technical

Assessment report of groundwater quality beneath the generating site and associated Ash

Disposal Facility (ADF) was undertaken (report 5 and 6 listed above). These reports are

included as environmental reports to this IE Licence review application as the following

attachments:

Attachment-7-1-3-3-Rec Env Report_ Hydrogeo Report

Attachment-7-1-3-3-Rec Env Report_Hydrogeo Report_2

The WOP station undertakes a groundwater monitoring programme which samples a

number of boreholes across the site in compliance with the requirements of the EPA IE

Licence P0611-02. Groundwater monitoring data for 2014 to 2017 has been compiled and

reviewed and presented in these AER reports (report 1 listed above) and monitoring results

are available within the Annual Environmental Reports (AER), see the following attachments:

Attachment-7-1-3-1_AER 2014;

Attachment-7-1-3-1_AER 2015;

Attachment-7-1-3-1_AER 2016; and

Attachment -7-1-3-1_AER 2017.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33

9

4. Preparing the Report

Table 4-1 presents the main stages when preparing a screening assessment and it

corresponding section in this report.

Table 4-1: Stages in the preparation of a Baseline Assessment

Stage Activity Objective Section

1.

Sc

ree

nin

g S

tag

es

Identify which hazardous substances

are used, produced or released at the

installation and produce a list of these

hazardous substances.

Determine whether or not

hazardous substances are

used, produced or released in

view of deciding on the need to

prepare and submit a baseline

report.

Section 5

2. Identify which of the hazardous

substances from Stage 1 are relevant

hazardous substances. Discard those

hazardous substances that are

incapable of contaminating soil or

groundwater. Justify and record the

decisions taken to exclude certain

hazardous substances.

To restrict further

consideration to only the

relevant hazardous

substances in view of deciding

on the need to prepare and

submit a baseline report.

Section 6

3. For each relevant hazardous

substance brought forward from Stage

2, identify the actual possibility for soil

or groundwater contamination at the

site of the installation, including the

probability of releases and their

consequences, and taking particular

account of:

the quantities of each hazardous

substance or groups of similar

hazardous substances concerned;

how and where hazardous

substances are stored, used and

to be transported around the

installation;

where they pose a risk to be

released;

In case of existing installations

also the measures that have been

To identify which of the

relevant hazardous

substances represent a

potential pollution risk at the

site based on the likelihood of

releases of such substances

occurring. For these

substances, information must

be included in the baseline

report. Section 7

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


10


adopted to ensure that it is

impossible in practice that

contamination of soil or

groundwater takes place.

4.

Bas

eli

ne

Re

po

rt P

rep

ara

tio

n

Provide a site history. Consider

available data and information:

In relation to the present use of the

site, and on emissions of

hazardous substances which have

occurred and which may give rise

to pollution. In particular, consider

accidents or incidents, drips or

spills from routine operations,

changes in operational practice,

site surfacing, changes in the

hazardous substances used.

Previous uses of the site that may

have resulted in the release of

hazardous substances, be they the

same as those used, produced or

released by the existing

installation, or different ones.

Identify potential sources

which may have resulted in the

hazardous substances

identified in Stage 3 being

already present on the site of

the installation.

Section 8

5 Identify the site’s environmental setting

including:

Topography;

Geology;

Direction of groundwater flow;

Other potential migration pathways

such as drains and service

channels;

Environmental aspects (e.g.

particular habitats, species,

protected areas etc.); and

Surrounding land use.

Determine where hazardous

substances may go if released

and where to look for them.

Also identify the environmental

media and receptors that are

potentially at risk and where

there are other activities in the

area which release the same

hazardous substances and

may cause them to migrate

onto the site.

Section 9

6 Use the results of Stages 3 to 5 to

describe the site, in particular

demonstrating the location, type,

extent and quantity of historic pollution

Identify the location, nature

and extent of existing pollution

on the site and to determine

which strata and groundwater

Section

10

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


11


and potential future emissions sources

noting the strata and groundwater

likely to be affected by those emissions

– making links between sources of

emissions, the pathways by which

pollution may move and the receptors

likely to be affected.

might be affected by such

pollution. Compare with

potential future emissions to

see if areas are coincident.

7 If there is sufficient information to

quantify the state of soil and

groundwater pollution by relevant

hazardous substances on the basis of

Stages (1) to (6) then go directly to

Stage 8. If insufficient information

exists then intrusive investigation of

the site will be required in order to

gather such information. The details of

such investigation should be clarified

with the competent authority.

Collect additional information

as necessary to allow a

quantified assessment of soil

and groundwater pollution by

relevant hazardous

substances. Section

11

8

Bas

eli

ne

Re

po

rt

Co

nte

nt

Produce a baseline report for the

installation that quantifies the state of

soil and groundwater pollution by

relevant hazardous substances.

Provide a baseline report in

line with the IED.

Section 9

– 12

represent

s the

Baseline

Report

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


12

5. Stage 1: Identifying the hazardous substances that are currently

used, produced or released at the installation

5.1 Guidance Requirements

Further to the objectives for Stage 1 detailed in Table 4.1 the following is required

under the Commission guidance:

Produce a list of all hazardous substances dealt with inside the installation

boundary (either as raw materials, products, intermediaries, by-products,

emissions or wastes). This should include all hazardous substances associated

with both the IED Annex I activities and directly associated activities which have

a technical connection to the activities carried out and which could have an effect

on soil or groundwater pollution.

Where hazardous substances are listed under trade names the chemical

constituents should also be identified. For mixtures or compounds the relative

proportion of the largest constituent chemicals should be identified.

5.2 Facility Details

The ESB WOP Station is a 150 MWe combustion plant with the ability to fire on peat.

Gas oil is also used to commence firing at start-up phase. Electricity from the facility is

exported into the National Grid. The primary bulk raw materials includes the fuel to be

combusted. There are also a variety of wastes arising from the peat combustion and

environmental control operations on the site. Ash from the combustion process is

disposed of at the dedicated Ash Disposal Facility (ADF). The sites activities are

controlled under the IE Licence for the Site (Licence P611-02) issued by the EPA and

an AER is prepared and submitted for the site. A list of all substances and mixtures

used and produced at the WOP station has been provided as Attachment-4-6-2-Raw-

Material-Interm-Products to the IE Licence review application.

5.3 Substances used and generated at the Station & ADF

The main substances used or produced in the generation of electricity at WOP include:

Peat which is delivered by train and truck to WOP, enters the station through

the Intermediate Peat Storage area (IPS) which is capable of storing 8400

tonnes of peat; and is transferred by conveyor belt system to the day silos. Peat

is a flammable material.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


13

Gas oil (Diesel) is delivered by road tanker and stored in a 200 m3 bunded

tank. Diesel is a flammable material.

Pulverised Fly Ash (PFA) and Bottom Fly Ash (BFA) which arises from the peat

combustion process are deposited in the stations ADF.

Potentially leachate is generated at the ADF site as a result of the disposal of

ash from the WOP station.

Water from the River Shannon for use as Cooling water and process water.

Cooling water is abstracted and used in a once-through cooling water cycle and

discharged back into the Shannon. Process water is also abstracted and

treated for use in the boiler and subsequently discharge back into the River

Shannon.

A number of other chemical substances are used at WOP to support the water

treatment process (e.g. Ammonia), the wastewater (foul water) treatment

system, the onsite station laboratory and general maintenance works

throughout the station and the ADF. Table 5-1 presents the chemicals stored in

significant volumes on site.

There are a number of surface water discharges from the station and the ADF

which are licensed under the existing IE licence. This includes the discharge of

the cooling water, boiler blowdown, water treatment effluent, treated foul water

from the onsite sewage treatment system and storm water, see further details in

Attachment-4-8-1-Operational Report to this IEL review application

Table 5-1: Major chemicals stored on site

Chemical Container Volume

Caustic Soda (NaOH) 30m3

Sulphuric Acid (H2SO4) 30m3

Caustic Brine 30m3

Ammonia (NH3) 1m3

Diesel (gas oil) 200m3 (auxiliary diesel generator)

1m3 (Diesel tank fire ware pump)

1.3m3 (emergency diesel generator tank)

25 m3 (locomotive fuel)

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:33


14

Chemical Container Volume

2 x 2.3 m3 (other use)

Lubricating Oil 8 m3

Gear Oil 2.3 m3

Antifreeze 1 m3

Waste Oil 1 m3

Further details of the substances and mixtures used and produced at the WOP station

have been provided as Attachment-4-6-2-Raw-Material-Interm-Products to the IE

Licence review application.

.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34

15

6. Stage 2: Identifying the relevant hazardous substances


Stage 2 as outlined in the commission guidance requires the following:

From the list produced in Stage 1, determine the potential pollution risk of each

hazardous substance by considering its chemical and physical properties such as:

composition, physical state (solid, liquid, and gas), solubility, toxicity, mobility,

persistence, etc. This information should be used to determine whether or not the

substance has the potential to cause pollution of soil and groundwater. The data,

together with the rationale used to interpret it, should be presented so it is clear in

the baseline report why substances have been excluded or included.

6.2 Identified Hazardous Substances

Based on the materials detailed in Attachment-4-6-2-Raw-Material-Interm-Products and

their quantities stored or produced, the substances considered relevant for this

assessment therefore include:

1. Major chemical stored onsite;

o Caustic Soda (NaOH);

o Sulphuric Acid (H2SO4);

o Caustic Brine;

o Ammonia (NH3);

o Diesel (gas oil);

o Lubricating Oil

o Gear Oil,

o Antifreeze; and

o Waste Oil

2. ADF Leachate (if and when generated); and

3. Operational Discharges such as process and wastewater and the associated site

drainage infrastructure.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


16

7. Stage 3: Assessment of Potential Pollution Risk



Each substance brought forward from Stage 2 should be considered in the context

of the site to determine whether circumstances exist which may result in the release

of the substance in sufficient quantities to represent a pollution risk, either as a

result of a single emission or as a result of accumulation from multiple emissions.

7.2 Chemical Storage, Handling & Management

The following storage and handling condition is stipulated under the IE Licence:

3.6 Tank, Container and Drum Storage Areas

3.6.1 All tank, container and drum storage areas shall be rendered

impervious to the materials stored therein. Bunds shall be designed having

regard to Agency guidelines ‘Storage and Transfer of Materials for

Scheduled Activities’ (2004).

3.6.2 All tank and drum storage areas shall, as a minimum, be bunded,

either locally or remotely, to a volume not less than the greater of the

following:

(i) 110% of the capacity of the largest tank or drum within the

bunded area; or

(ii) 25% of the total volume of substance that could be stored within

the bunded area.

3.6.3 All drainage from bunded areas shall be treated as contaminated

unless it can be demonstrated to be otherwise. All drainage from bunded

areas shall be diverted for collection and safe disposal, unless it can be

deemed uncontaminated and does not exceed the trigger levels set for

storm water emissions under Condition 6.13 of this licence.

3.6.4 Within six months of the date of grant of this licence, all inlets, outlets,

vent pipes, valves and gauges must be within a bunded area.

3.6.5 All tanks, containers and drums shall be labelled to clearly indicate

their contents.

In addition, Condition 6.9 of the IEL Licence requires the following:

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


17

The integrity and water tightness of all underground pipes, tanks, bunding

structures and containers and their resistance to penetration by water or other

materials carried or stored therein shall be tested and demonstrated by the

licensee within twelve months from date of grant of licence. This testing shall be

carried out by the licensee at least once every three years thereafter and reported

to the Agency on each occasion. This testing shall be carried out in accordance

with any guidance published by the Agency. A written record of all integrity tests

and any maintenance or remedial work arising from them shall be maintained by

the licensee. A report on such tests shall be included in the AER. the site is

required to complete.

The adherence to the above conditions forms part of ongoing environmental monitoring

and management at the site. The most recent bund integrity testing was completed during

2017. All bund are currently compliant , 2017 was the last suite of testing and any failures

were repaired and retested and it is detailed in the AER on an annual basis

The WOP station and ADF is certified to ISO14001. There is an appointed environmental

committee for the site which sits biannually. This committee is responsible for the

implementation of the following good environmental practices aimed at reducing risks

from potential spills and leaks;

All chemicals listed in 6.2 are bunded and/or stored in double skinned containers;

In-house environmental audits are completed regularly ;

All bunds are alarmed;

Bunds are inspected monthly and alarms tested biannually;

Oil tanks are filled to maximum of 75% of their total capacity.

Chemical tanks are filled to maximum of 90% of their total capacity.

7.3 Leachate from the ADF

The ADF is an engineered landfill currently comprising five cells complete with a geo-

synthetic clay liner (GCL) at the base of each cell. Cells 1-3 are already closed and

capped. Cell 4 and 5 are currently in operation. The GCL consists of sodium bentonite

clay, supported by geotextiles, which forms another hydraulic barrier, to prevent leachate

migration to groundwater. The landfill is subdivided into cells which are filled sequentially.

The GCL is overlain with a composite drainage layer (CDL), which collects any leachate

generated. The CDL drains to a leachate collection drainage system at one end of each

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


18

cell, which transfers leachate to a leachate monitoring manhole and from there to a

temporary storage lagoon where it is allowed to settle. Leachate when produced in the

cells is managed through both recirculation and discharge. Once the leachate complies

with the ELVs set out in Section B of License P0611-02, it is discharged to the Gowlan

River north of the ADF. Surface water emissions limits for Ash Disposal Lagoon Outfall

(AL-SW1) are included in Schedule B.2 Emissions to Water of the Existing Licence and

are detailed in Table 7-3.

Table 7-1: Leachate Emission Limits

Source Parameter Emission Limit Value

Ash Disposal Lagoon Outfall (AL-SW1)

pH 6 - 9

Suspended Solids 35 mg/m3

Toxicity 5

In addition to AL-SW1 monitoring point, there are four groundwater monitoring locations

(ADF-GW3 to ADF-GW6) at the ADF site, see Site plan QS-000139-01-D460-020. These

locations are monitored and reported in the AER with regards to Groundwater Threshold

Values (GTVs) (where available) set out in the European Communities Environmental

Objectives (Groundwater) Regulations, 2010 as amended.

7.4 Operational Discharges

There are five sources of operational discharges to surface water within the station and

one within the ADF. These discharges are include;

1. Cooling water;

2. Screen wash water (surface water intake screen);

3. Boiler blowdown;

4. Water treatment effluent;

5. Treated foul water from the onsite sewage treatment system; and

6. Leachate from the ADF cells.

In addition, there are also discharges from the surface water drainage system i.e. storm

water (SW6 and SW7). Surface water from the station is discharged from emission points

SW1, SW2, SW3, SW4 and SW5 and the emission limits are included in Schedule B.2 of

the IE Licence.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


19

In accordance with EMS 9.1-05, site drainage (including storm water, process and foul)

testing was carried out in 2014, 2017 and 2018. All drainage on site, including drains,

manholes were tested and any defects identified in the 2014 surveys have been repaired.

In 2017 the septic tank, anoxic tank and foul effluent pump sump were emptied and

internal inspections carried out on the septic and anoxic tanks. Internal inspections show

no structural issues in either tank. However, following concerns relating to ground or river

water entering the foul effluent system, inspections and surveys were carried out to

determine the source. The potential area was narrowed down to an estimated 6m gravity

drain from the septic tank to the anoxic tank. The 2017 survey and report recommended

that drains on site should be cleared and washed out, and a drain survey carried out to

determine if ground or river water is entering the drainage system. The surveys including

hydrostatic testing were completed in October 2018. The station is commencing a repair

programme in 2019 in relation to any failed drains from the previous clean and test

programme conducted in 2018

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


20

Table 7-2: Surface Water Discharge Emission Limits

Source Parameter Emission Limit Value

Cooling and

Screen Wash

Water

(PS-SW1 &

PS-SW2)

Thermal load 186 MWth

Residual Chorine

0.1 mg/l2

pH 6 - 8.5

Sewage Treatment Effluent

(PS-SW3)

pH 6 - 9

Temperature 25OC

BOD 20 mg/l

Suspended Solids

30 mg/l

Boiler Blowdown

(PS-SW4)

Temperature Condition 5.5 - Discharges from the installation shall not artificially increase the ambient temperature of the receiving water by more than 1.5oC outside the mixing zone. In relation to temperature, the mixing zone shall not exceed 25% of the cross sectional area of the river at any point.

pH 6-9

Ammonia (as N) 1 mg/l & 0.07 kg/day

Sulphate (as SO4)3

0.5 mg/l

Water Treatment Effluent

(PS-SW5)

Temperature 25oC

pH 6-8.5

Toxicity 10 TU

BOD 20 mg/l

Suspended Solids

30 mg/l

Total Dissolved Solids

30,000 mg/l

Ammonia (as N) 1.5 mg/l & 21.9kg/annum

The ELV is 50mg/l during condensate polisher plant regeneration only

2 Agreed with the EPA on the 20/12/2013- submission LR006046, “not to conduct residual chlorine monitoring on PS-SW1 and SW-2 3 Agreed with the EPA on the 23/06/2017- submission LR029247 not to conduct sulphate monitoring on PS-SW4.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


21

7.5 Stage 3 Summary

The relevant hazardous substances at WOP Station and the ADF identified in Stage 2

include the following:

Major chemical stored onsite;

Leachate; and

Operational Discharges.

The potential for chemicals, ash leachate and process discharges to pose an

environmental risk is low with the current controls, i.e. storage and drainage infrastructure,

the landfill cell design and surface water management systems and monitoring. However,

due to the sensitive nature of the receiving environment namely the River Shannon and

its associated ecological designations4, a Baseline Report has been compiled for this IE

Licence Review application.

4 The station site is adjacent to the River Shannon and is adjacent to the River Shannon Callows Special Area of Conservation (SAC -Site Code 002160) and the Middle Shannon Callows Special Protection Area (SPA – Site Code 004096). The ADF site is over 3.5 km from the Callows SAC/SPA, is 2.5 km from the Mongan Bog SPA/SAC and 1 km from the Fin Lough SAC.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


22

8. Stage 4: Site History



The purpose of this section is to determine which of the relevant hazardous

substances identified by Stage 3 have the potential to be present on site in the soil

and groundwater already as a result of activities to date and to determine whether

they are coincident with potential future emission points.

8.2 Site History and Overview

Construction of the original Shannonbridge Generating Station began in the late 1950’s

and there has been continuous production of electricity at the site since 1965 when a 40

MW unit was first commissioned. That station was extended in 1977 and again in 1982

when at which point it had an installed electrical capacity of 125 MW. The EPA issued an

Integrated Pollution Prevention and Control (IPPC) licence (Reg. No. P0626-01) for the

site in April 2003.That station was decommissioned in 2003 and the site was remediated

to the satisfaction of the EPA. The established character and use of the WOP site is

industrial – reflecting its long established use for electricity generation activity.

An environmental exit audit for the original Shannonbridge Generating Station was carried

out in 2009 which assessed soil and groundwater quality beneath the former ash ponds

within the former ESB Power Station at Shannonbridge. Power generating activities

ceased in 2004 and the demolition of the former station buildings was completed in 2009

prior to the exit audit.

The existing station (a 150MW unit) was commissioned by ESB in 2005 as required by

the Electricity Regulation Act 1999 (Public Service Obligations) Order 2002 (SI

No.217/2002). It is a peat-fuelled generation station with an installed capacity of 150 MW

electric. It operates under an IE Licence (P0611-02) issued by the EPA. The footprint of

the previous Shannonbridge units and the former, now decommissioned, ash disposal

facility lie outside the site IE Licenced boundary of WOP generating station.

The site accommodates structures and activities typical of a generating station, including

fuel (principally peat with relatively small volumes of oil used for start-up and combustion

support), storage and handling areas and associated plant; the generation station itself;

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


23

and a range of ancillary services including water treatment and management systems,

offices and administration area.

8.2.1 Ash Disposal Facility

The station’s off-site ADF is located on remote Bord na Móna cutaway bogland at

Clonfinlough, Co. Offaly, approximately 8 km from the power station. The ADF site area

extends to approximately 35 ha. The deposited ash comprises bottom ash and fly ash. Of

the total ash arising, approximately 5% is bottom ash and the remainder is fly ash. The

facility is operated by Bord na Móna on the station’s behalf. The ADF operates under the

same IE licence as the station – Licence P0611-02.

Fly ash and bottom ash are transported to the ADF on Bord na Móna’s narrow gauge rail

system in specially designed saddleback wagons. One train (rake), each containing up to

12 wagons, is used daily, Monday – Saturday. Each wagon comprises two covered ash

buckets with combined capacity of approximately 7-9 m³ of ash. The ash is tipped from

the wagons and is placed in the cells using low bearing pressure tracked earthmoving

plant. The ash is placed semi-dry and is wetted to control potential dust emissions. It is

graded to fall during the filling of the cells to ensure that ponding, resulting in leachate

generation, does not occur. A tractor drawn spray tanker or fixed spray system is used in

wetting the ash to aid compaction and further prevent dust nuisance. Leachate produced

in the cells is managed through both recirculation and discharge. Discharge to the Gowlan

River north of the ADF is undertaken in compliance with the ELVs set out in Section B of

License P0611-02. Three cells (Cells 1, 2 and 3) are already closed and capped, and Cell

4 is operational and partially capped. It is proposed to cap the remaining area of Cell 4

during this year and will be completed next year and Cell 5 is also operational.

Cover and capping that is already in place for completed cells comprises a 1 m layer of

peat / subsoil, which was added in a concave mound design. It is revegetated to blend

with the natural landscape. Cells 1-4 have a basal and capping liner (permanent low

permeability Geosynthetic Clay Liner). From Cell 5 all cells will be entirely lined. The

material to be used for the restoration layer will be a mixture of peat and soil and shall be

sourced on site from existing uprisings stockpiles and cutaway bog within the site

boundary. It is anticipated that Cell 6 will be used from late 2019 / early 2020 and will be

actively in-use when the WOP Station enters its co-firing phase transitioning from peat to

biomass. That cell will be required for acceptance of ash up until end of 2020.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


24

It is proposed that a further five engineered landfill cells will be developed (Cells 7, 8, 9,

10 and 11). This will extend the ADF footprint by c.173,130 sq.m. This will accommodate

the disposal of an additional c. 929,200 cubic metres of ash (approximately equivalent to

880,000 tonnes). As noted above, this facility will have no defined date of closure but it is

expected it can accommodate ash arisings for a period in the range of 25 years.

To facilitate the extended operation of the ADF, peat soil within the ADF site area and

adjacent to the landfill footprint itself will also be excavated to a depth of circa one metre

to provide material for the final landfill capping layer.

Cells will continue to be capped as they are filled.

8.3 Exit Audit of the former ESB Power Station at Shannonbridge

The environmental exit audit which was as carried out in 2009 assessed soil and

groundwater quality beneath the former ash ponds within the former ESB Power Station

at Shannonbridge. The audit concluded the following:

Soil and water quality in the subject area is not considered to pose a risk to future

site users in a continued industrial/commercial landuse scenario assuming

groundwater and surface water (north and south drains) within the subject area

will not be used as drinking water.

The subject area is considered to be “asbestos safe” as per the ESB brownfield

policy.

The risk to controlled waters from shallow soil, shallow groundwater and surface

water quality in the subject area is considered to be low.

8.4 WOP EIS 2001

An Environmental Impact Statement (ESB, 2001) for the WOP station detailed that:

“Ammoniacal nitrogen was found to exceed the EU Drinking Water Limit for

ammonia of 0.3 mg/l in all eight groundwater samples. Concentrations were

between 3.5 mg/l and 11.4 mg/l. Ammoniacal nitrogen may be naturally present in

groundwater as it is formed by the microbial reduction of other nitrogen

compounds. However, it can also be sourced from foul and industrial wastes that

may be released to the groundwater by septic tanks, agricultural slurry pits, etc.

The widespread occurrence and relative close range of concentrations would

suggest that the ammoniacal nitrogen levels in the groundwater at the site

represent the background concentration range.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


25

Elevated concentrations were recorded for nitrite (0.05 mg/l, 0.12 mg/l and 0.14

mg/l, which exceed the EU Drinking Water Limit of 0.03 mg/l), Chemical Oxygen

Demand (44 mg/l to 241mg/l, which exceed the EU Surface Water (A3) Limit of 40

mg/l,), faecal coliforms (between 1 cfu/100 ml and 23 cfu/100 ml) and total

coliforms (all >180 cfu/100 ml). These determinands, in a similar manner to

ammoniacal nitrogen, may be associated with foul water discharges.

However, foul water discharge seems unlikely as a source of groundwater

contamination given the location of the site. The elevated Chemical Oxygen

Demand may be due to the presence of significant levels of Organic Carbon in the

water. The organic material in the water would provide a substrate for bacterial

metabolism and this may expand the presence of the coliforms. Where elevated

levels of these four determinants were recorded, they are considered to be

representative of the higher end of the natural background range.

A zinc concentration of 2,810 μg/l, exceeding the EU Drinking Water Limit (1,000

μg/l), was reported in one groundwater sample. This concentration is well above

the other groundwater samples where the highest concentration was 136 μg/l.

Calcium and Iron were found to exceed their respective EU Drinking Water Limits

in two samples. Potassium exceeded the EU Drinking Water Limit (12 mg/l) in two

samples with concentrations of 29 mg/l and 33 mg/l. Elevated concentrations of

calcium, Iron and potassium are thought to be associated with the overburden and

bedrock chemistry and are thus representative of the higher end of the natural

background range. Five of the seven groundwater samples had manganese

concentrations above the EU Drinking Water Limit (50 μg/l) with concentrations

ranging from 81 μg/l in to 699 μg/l. Elevated manganese concentrations are also

thought to relate to bedrock and groundwater geochemistry and are considered to

represent natural background concentrations.

Elevated concentrations of DRO, mineral oil, total phenol and total PAH were

reported in one to two groundwater samples. These elevated hydrocarbon

concentrations are generally not significantly above the concentrations

encountered in the other groundwater samples and may be due to the introduction

of hydrocarbons during fieldwork. It is also possible that the hydrocarbons

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


26

encountered are related to the natural levels and are at the upper end of the

natural range.

Hydrocarbons can be derived from the natural breakdown of larger naturally

occurring organic molecules and the soil samples may, therefore, be more organic

rich than the other samples tested.

In general, while some analytes were at the higher end of their naturally occurring

ranges, the groundwater did not show significant contamination.”

8.5 WOP EIAR 2017

An EIAR was prepared in 2018 to support a planning application to transition WOP from

peat to biomass. As part of this EIAR, environmental soil and groundwater samples were

collected from existing and new boreholes and trial pits in 2017. Samples were analysed

by a UKAS ISO 17025 accredited lab. Results are discussed and incorporated in Section

6 below.

8.6 Site Infrastructure

A certified EMS is in place with procedures for inspection and maintenance of storage

equipment, bunds and drains. The following are the relevant EMS procedures followed on

site;

EMS 11.2-04 Procedure for Testing Bunds Safety Shower Checks.

EMS 11.2-12 Procedure for Inspection and Cleaning of Interceptor.

EMS 9.1-05 Procedure for Maintenance of Drains, Sewers and Pipelines.

8.7 Incident History

The site has a long history of industrial use. However no major incidents, with the

potential to negatively impact soil or water quality, have occurred on site since the

commissioning of WOP station in 2004. Minor incidents have been reported to the EPA as

they occurred within the AERs.

It is noted that a non-compliance in relation to a breach of a quarterly ELV for ammonia

occurred as sampling was undertaken after a condensate polisher regeneration (ammonia

ELV is 50mg/l for a CPP regen) in 2017. WOP station subsequently undertook and

submitted to the EPA additional analysis on this sampling point for approximately two

months to demonstrate compliance with the required ELV. No further action was required.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


27

9. Stage 5: Environmental Setting


Stage 5 as outlined in the commission guidance, requires the following:

As a result of Stages 1-4 the locations on the site are identified where future

emissions could occur and where emissions may already have occurred. Stage 5

aims to determine the fate of any such emissions, the strata and groundwater

which may be affected and to establish the extent and depth to which the land

needs to be characterised. This requires an understanding of the characteristics of

the ground and groundwater at the site as well as the surrounding areas that may

influence the site of the installation itself.

Where available, site specific data should be used. When not available use

reference data, qualitative/subjective assessment, inferred or extrapolated data. In

each case the source of the data should be identified, and where this is not site

specific justification for the use of the selected data and include details of any

margins of error which apply.

9.2 Topography

Power Station: West Offaly Power is located approximately 25 km south of Athlone and

approximately 15 km east of Ballinasloe. Immediately south of the site, the River Suck

flows into the River Shannon. The River Shannon is the dominant feature of the

landscape, with all other water bodies in the area flowing into it. The power station site is

at an elevation of 35m – 45m above OD.

Ash Disposal Facility Site: The station’s off-site ADF is located on remote Bord na

Móna cutaway bogland near Derrylahan, Co. Offaly, approximately 8 km from the power

station. The ADF site area extends to approximately 35 ha. The ADF consists of full cells

(which have been filled to capacity and are now capped) and active ash cells (cells still in

use). The area surrounding the ADF site is used by Bord Na Mona for the production and

storage of milled peat. The ground level in the disposal area lies between 35 – 40 m OD

(ESB, 2001). As part of the proposed planning to transition of WOP from peat to biomass

fuel, the ADF will be expanded and will extend over an additional circa 17.3 ha.

9.3 Geology and Hydrogeology

Power Station: The Teagasc soils layers indicates that the site is underlain to the west

and northwest by mineral Alluvium soils and Made ground (at the site of the former

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


28

Shannonbridge Power Station). Part of the site to the northwest sits on Peat Gleys Basic

parent materials with the reminder of the site comprising Grey Brown Podzolics and

surface water and Ground water Gleys derived chiefly from limestone. The main WOP

station site is indicated as being underlain by Alluvium undifferentiated gravelly subsoil to

the west, with Basic esker sands and gravels to the east. The central area of the site

comprises Made ground.

Information from GSI indicates the underlying bedrock is Dinantian Upper Impure

Limestone. Teagasc have identified the subsoil beneath the west of the site as being

Alluvium. The eastern portion of the site is underlain by Till derived chiefly from limestone.

Shallow groundwater is present in the soils above the bedrock. Due to the nature and

extent of this groundwater, this water is not classified as an aquifer by the GSI. The

bedrock aquifer beneath the site is classed as Locally Important (Ll) which is moderately

productive only in local zones. The bedrock below the site is karstic meaning that high

groundwater flows and yields may be encountered in discrete zones. GSI mapping

indicates that the station site is located on two main vulnerability classes, Moderate

vulnerability to the west and High vulnerability to the east. Overall, the flow direction is

likely to be towards the Shannon River to the west and southwest of the groundwater

body.

The GSI database indicates that the nearest two groundwater abstraction wells are

located between 1 - 1.5 km to the north of the site (Raghra Townland adjacent to

Shannonbridge).

Ash Disposal Facility: The ADF is located on Cut-raised Bog cutaway/cutover soils. The

Subsoils beneath the ADF site are Cutover peat.

The GSI website indicates the site is underlain partially to the northwest by the Navan

Beds (Diantian Courcetyan dark Limestone, Mudstone and Sandstone) and mainly to the

southwest by the Ballystein Formation comprising Dark Muddy limestones and Shale. The

GSI Sheet No. 15 indicates that the site is underlain by Carboniferous Argillaceous

Bioclastic limestones (ABL) of Courceyan age. The ABL consists of dark grey

fossiliferous, argillaceous calcarenites interbedded with thin calcareous shales. The Sheet

indicates the presence of a north-east south-west trending fault approximately 1km to the

north of the site.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


29

The underlying bedrock aquifer is classified by the GSI as a locally important aquifer

(bedrock which is moderately productive only in local zones) with ‘low’ groundwater

vulnerability. There are no Source Protection Zones within 5 km radius of the site. Based

on groundwater elevation data collected in November 2000, groundwater flow direction is

towards the Gowan River northwest of the site.

The WOP station site and the WOP ADF site are located on the Clara groundwater body

(IE_SH_G_240) and is categorised as having a Good status

9.4 Hydrology

Power Station: Both the power station and the ADF are within the Shannon System

catchment and surface drainage ultimately enters this system. Both the Suck and the

Shannon Upper waterbodies are located upstream of WOP station and its discharges.

Process and drainage water from the station site is discharged directly to the River

Shannon.

The Water Framework Directive (WFD) status of the Shannon (Shannon (Lower) 010) is

unassigned. There are seven discharges from the site to the (Shannon (Shannon (Lower)

_010 under the existing IE licence and all are monitored in accordance with IE Licence

No. P0611-02.

Ash Disposal Facility: The ADF is located within an area of cutaway Bord na Móna

commercial peatland located at Derrylahan. There is one surface water discharge point

under the IE licence from the ADF. This discharge point is located on the Blackwater

(Shannonbridge) _020 (known also as the Gowlan River), a tributary of the River

Blackwater, and north of the ADF. The WFD status of the Blackwater (Shannonbridge)

_020 is good.

Any leachate discharged from the ADF to the Blackwater (Shannonbridge) _020 is done

under the existing IE licence and is monitored in accordance with IE Licence No. P0611-

02.

9.5 Surrounding land use

Power Station: The site is situated south of the village of Shannonbridge and is not

adjacent to or affected by other industries which have the potential to cause pollution to

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


30

migrate onto the site. The site is bound to the east by the river Shannon, agricultural fields

to west and north and commercial and residential to the to the south and north.

Ash Disposal Facility: The ADF site is located at Derrylahan, 6.5 km north east of the

WOP site. It occupies an area of 36 ha located within 800 ha of commercial Bord na

Móna peat harvesting land.

9.6 Natural Habitats

The station site is adjacent to the River Shannon and there are several designated sites

located within 15km of WOP Station and the ADF. This includes the River Shannon

Callows SAC and several SAC and SPA sites in the surrounding bogland area. More

details of the Biodiversity in relation to the station and ADF sites is contained within the

following attachments:

Attachment-7-1-3-3-Rec Env Report_AA Screening

9.7 Conceptual Site Model

The Conceptual Site Model (CSM) describes the potential sources of contamination at the

site, the potential migration pathways along which it could migrate and the sensitive

receptors it could impact upon. Figure 9-1 and Figure 9-2 below presents the CSM

identifying the Source-Pathway-Receptor linkages for the station and the ADF compiled

by AECOMin their Risk Screening and Technical Assessment report. A CSM graphical

representation produced by AECOM is presented in Appendix 2 for the station and the

ADF.

Figure 9-1: Station CSM

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


31

Figure 9-2: ADF CSM

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


32

10. Stage 6: Site Characterisation


Stage 6 as outlined in the Commission guidance requires the following:

A description of the site should in particular demonstrate the location, type, extent

and quantity of historic pollution and potential future emissions sources noting the

strata and groundwater likely to be affected by those emissions.

10.2 Summary of Groundwater Quality, AECOM Risk Screening and Technical

Assessment, 2015

A comprehensive risk based screening assessment of groundwater quality beneath the

site was undertaken by AECOM in 2015 to address Condition 6.14.3 of the IE License. All

available reports and data were considered up to 2015 as part of this assessment.

AECOM produced the following two reports as part of this assessment and in consultation

with the EPA. The reports were completed in accordance with the EPA Guidance on the

Authorisation of Discharges to Groundwater (2011);

AECOM, Risk Screening and Technical Assessment, IEL P0611-02,

Ref:47092932, 20 August 2015 (Attachment-7-1-3-3-Rec Env Report_ Hydrogeo

Report);

AECOM WOP Further Environmental Assessment 2015, Ref 47093108, 13

November 2015 (Attachment-7-1-3-3-Rec Env Report_Hydrogeo Report_2).

The AECOM reports assessed available analytical groundwater data against screening

criteria generated from the following hierarchy;

European Communities Environmental Objectives (Groundwater) Regulations

(GTV), 2011 (Statutory Instrument No. 389 of 2011); and

Environmental Protective Agency’s draft Interim Guideline Values (IGVs) for the

Protection of Groundwater, 2003.

Elevated concentrations of Arsenic, Nickel, Sulphate, Potassium and Manganese were

reported above the screening criteria at the Station and the ADF. Table 10-1 presents the

exceedances identified by AECOM of 2014 analytical results (the most recent available

data set).

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:34


33

Table 10-1: Elevated Concentrations 2015 Report

Parameter Screening

Criteria

(ug/l)

Reported

Concentrations Range

of Exceedances (ug/l)

Exceeding Wells

- ADF

Exceeding

Wells -

Station

Arsenic 7.5 (GTV) 18 ADF – GW5 -

Nickel 15 (GTV) 15.3 ADF – GW5 -

Potassium 5000 (IGV) 24900 - 26700 ADF-GW4 PS-GW2

Sulphate 187.5 (GTV) 273 - PS-GW2

Manganese 50 (IGV) 58.3 - 550 ADF-GW3, ADF-

GW4, ADF-GW5

and ADF-GW6

PS-GW2

Table 10-2: 2015 Potential Risk Status

Parameter ADF

Exceeding

Wells

Station

Exceeding

Wells

Potential Source Identified Potential Risk

to Groundwater

Status*

Arsenic ADF –

GW5

- Sampling Methodology and

Background geology and

hydrogeology

Low

Nickel ADF –

GW5

- Sampling Methodology and

Background geology and

hydrogeology

Low

Potassium ADF-GW4

and ADF-

GW6

PS-GW2 Either background geology

and hydrogeology or Former

Ash disposal area located at

the station and leachate from

the ADF.

Low

Sulphate - PS-GW2 Former Ash disposal area

located at the station

Low

Manganese ADF-GW3,

ADF-GW4,

ADF-GW5

PS-GW2 Background geology and

hydrogeology

Low

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


34

Parameter ADF

Exceeding

Wells

Station

Exceeding

Wells

Potential Source Identified Potential Risk

to Groundwater

Status*

and ADF-

GW6

Chloride ADF-GW4 - Leachate levels generated

were above the lined section

(1.0 m height) of the cell and

therefore leachate reportedly

seeped out over the lined

portion of the cell. The

Operational plan was revised

in 2014 and new agreement

was reached with the EPA in

2014 regarding the liner and

capping requirements.

Low

*2015 AECOM reports

Since 2011, Total Petroleum Hydrocarbons (TPH) have not been detected at

concentrations exceeding the LOD (1 mg/l). However, it should be noted that the LOD is

greater than the GAC of 0.01 mg/l.

The following are the main conclusions detailed in the AECOM2015 reports:

Potential risks to groundwater were identified from elevated concentrations of

arsenic, nickel, potassium and sulphate. Further monitoring is recommended to

identify any significant upward trends and to confirm or otherwise the potential

risks and to demonstrate compliance with the Groundwater Regulations.

Given that the elevated concentrations of arsenic, nickel, potassium and sulphate

were less than100 times the GAC, the risk to the overall status of the groundwater

body is considered to be low.

An area to the south of the site (the station) is identified as a potential risk to

controlled waters, as it contains landfilled waste materials from the former power

station. It is recommended that a groundwater sample is collected down hydraulic

gradient of this area to assess possible impact to the groundwater body and to

demonstrate compliance with the Groundwater Regulations.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


35

Bunds were observed to be in a good condition. Bund integrity testing was

completed in 2014 and it was reported to AECOM that all bunds passed the

respective integrity tests. Good environmental management practices are in place

to reduce the risk of spills to the environment.

As each cell within the landfill reaches capacity, it is capped with a permanent low

permeability GCL and as a result, leachate production at the ADF will eventually

cease.

It is recommended that alternative analysis for hydrocarbons is used with an LOD

<10ug/L to screen for potential hydrocarbons.

The EPA requested further information and this was furnished through a second report

issued (AECOMWOP Further Environmental Assessment 2015, Ref 47093108) in

November 2015. To address the EPA queries, additional testing and assessment was

completed as part of this report.

AECOM reported that the sampling methodology undertaken to collect groundwater

samples likely contributed to the elevated concentrations detected. Their additional

assessment of the ADF leachate determined that Arsenic and Nickel concentrations were

below their respective GAC. Consequently the potential risk from the ADF leachate to the

underlying groundwater was considered to be low.

Elevated potassium concentrations were reported at the ADF and the station indicating a

potential risk to the underlying groundwater. The risk is determined as low given that the

elevated concentrations are 100 less than the GAC for potassium and associated with

natural background levels (EIS 2001).

The following conclusions were drawn by AECOM following their additional sampling,

testing and assessment undertaken in “the Former Dump Area” of the former station:

Asbestos Containing Material (ACMs) were present in eleven of the seventeen

test pits excavated. All ACM observed was beneath the surface and mostly in a

bound form. Lose fibrous material was also encountered at depths of between

1.0m and 2.1meters below ground level. No ACM was observed on the surface.

Given that the observed ACM was in all cased buried, that no ACM was observed

on the ground surface and that the area has since been overlain by Bord na Mona

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


36

railway tracks, the generation of airborne asbestos fibres from the subject area

was considered unlikely.

A management system was recommended to be put in place to manage the risks

posed by the identified ACM, particularly in relation to any future excavation works

in the vicinity of the subject area.

10.3 ESB 2017 Site Investigation Soil Analytical Results

A geotechnical site investigation was undertaken in 2017 to support the Environmental

Impact Assessment (EIA) process in relation to the proposed transition to a full biomass

generating station and increasing the capacity of the ADF.

The extent of the investigation included boreholes by cable percussion boring and rotary

drilling, temporary groundwater well installations, trial pits, slit trenches, soil and

groundwater sampling, in-situ and laboratory testing, and the preparation of a factual and

geotechnical interpretative report on the findings.

Six temporary5 groundwater monitoring wells (WOP BH2/17, WOP BH4/17, WOP BH5/17,

WOP BH6/17, WOP BH9/17 and WOP BH11/17) were installed at the station. Three

temporary groundwater monitoring wells were installed at the ADF (WOP_ADF BH01/17,

WOP_ADF BH02/17, WOP-ADF BH03/17) and four IE Licence groundwater monitoring

wells (WOP ADF GW3, WOP ADF GW4, WOP ADF GW5, WOP ADF GW6).

As part of the Site Investigation, soil samples were collected from boreholes and trial pits

excavated across both the station and the ADF. Samples were transported under

standard Chain of Custody and analysed by a UKAS ISO17015 accredited laboratory.

Soil samples were collected from shallow soil at the Station and the ADF and compared

against risk based Generic Assessment Criteria (GAC) to assess the potential risk to

future site users. No significant visual or olfactory signs of contamination were identified

during the course of the site investigation. Soil analytical results are presented in

Appendix 3 and laboratory results presented in Appendix 4.

The GACs used are UK industry standard screening values produced by LQM/CIEH

(Land Quality Management Limited and Chartered Institute of Environmental Health)

5 It is planned that these wells will be decommissioned prior to the commencement of future construction works

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


37

Suitable 4 Use Levels (S4UL6) developed for a range of significant contaminant

parameters and generic land use settings including; in this case, the continued end-use

as a commercial land use and based on 1% Soil Organic Matter. The S4UL GACs are

generic toxicology based health criteria and represent an estimated contaminant

concentration, below which would likely pose a minimal potential risk to Human Health. If

detected concentrations are below the GAC, then the potential risks are not considered

significant. Concentrations above the GAC do not mean a significant risk is present, but

that further consideration is required in order to assess the potential residual risk to

Human Health.

This risk based approach is considered consistent with the Irish EPA guidance on

assessment of contaminated land at EPA Licenced facilities and a best practice approach

in Ireland for the assessment of residual risks associated with ground contamination.

Soil samples were tested for a range of the following parameters;

Metals including Aluminium, Arsenic, Barium, Cadmium, Chromium, Copper, Iron,

Lead, Mercury, Molybdenum, Nickel, Selenium and Zinc

Polycyclic Aromatic Hydrocarbons (PAHS)

Methyl Tertiary Butyl Ether

Benzene, Toluene, Xylene, Ethylbenzene

Total Petroleum Hydrocarbon (TPH)

Ammonicial Nitrogen,

Chloride,

Orthophosphate

Sulphate

Semi Volatile Organic Matter (SVOC)

Volatile Organic Matter (VOC)

Analytical results for all 17 samples collected and analysis at the Station and 16 samples

collected at the ADF, were below their respective GAC or the laboratory LOD. This,

together with the absence of any significant visual or olfactory signs of contamination,

indicate the potential risk to Human Health is low.

6 GACs generated using the UKEA Contaminated Land Exposure Assessment (CLEA)8 model

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


38

10.3.1 ESB 2017 SI Groundwater Monitoring Results

Following the completion of the 2017 Site Investigation, ESB undertook a groundwater

monitoring round sampling all groundwater wells present at the Station and the ADF.

An analysis of the groundwater monitoring data undertaken as part of the groundwater

monitoring round at the WOP station compared to the Groundwater Threshold Values

(GTVs) in the European Communities Environmental Objectives (Groundwater)

Regulations, 2010, (S.I. No. 9 of 2010) and surface EQS. The following parameters were

tested;

Dissolved Metals

PAHs

TPH CWG

BTEX

VOC and SVOC

Organochlorine & Organophosphorus Pesticides

Phenols

Ammoniacal Nitrogen

Chloride

Nitrate

Nitrite

Orthophosphate

Sulphide

Total Coliforms

Groundwater samples were collected at 7 locations across the Station site. The following

table presents the exceedances at the Station wells when compared to their respective

screening criteria. All other parameters were either not detected above the laboratory

lower limit of detection (LOD) or their respective screening criteria and are therefore not

considered further. Analytical results are presented in Appendix 5 and laboratory results

presented in Appendix 6.

Table 10-3: 2017 Station Groundwater Monitoring Results

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


39

Sample ID GW Regulations Screening

Criteria

WOP

BH02/17

WOP BH04/1

7

WOP BH05/1

7

WOP BH06/1

7

WOP BH09/1

7

WOP-PS-

GW1

WOP-PS-

GW2

Sample Date 11/05/2017

11/05/2017

11/05/2017

11/05/2017

11/05/2017

11/05/2017

10/05/2017

GTV IGV

Dissolved Aluminium #

150 (ug/l) 291 20 661 1083 20 20 20

Total Dissolved Iron #

200 (ug/l)

20 7588 21 69 20 242 1800

Dissolved Manganese #

50 (ug/l)

2 928 2 2 239 823 203

Dissolved Sodium #

150 mg/l 160.8

96.1 105 193.6 37.2 11 80.4

Sulphate as SO4 #

187.5 mg/l

120.9

191 310.9 108.3 162.8 41.3 248.6

Ammoniacal Nitrogen as N #

0.175 mg/l

3.69 2.44 6.72 21.29 1.78 0.04 9.81

Elevated dissolved aluminium concentrations (291 ug/l -1083 ug/l) were detected above

the GTV screening criteria (150ug/l) in 3 wells (BH02, BH05 and BH06) sampled at the

former ash landfill at the station. The concentrations detected indicate a potential risk to

the underlying groundwater. However the potential risk to the underlying groundwater is

low given the environmental site setting and that the elevated concentrations are 100 less

than the screening criteria for Aluminium.

Iron concentrations were found to be elevated in 3 wells (BH04, PSGW1 and PSGW2). It

has been previously assessed and reported by AECOM that elevated levels of Iron are

associated with overburden and bedrock chemistry in the area, see Section 9.4 above.

Consequently, the potential risk to the underlying groundwater is considered low given the

environmental site setting and the naturally elevated background concentrations.

Four of the seven groundwater samples had manganese concentrations above the

screening criteria (50 μg/l) with concentrations ranging from 203 μg/l in to 928 μg/l.

Elevated manganese concentrations are also thought to relate to bedrock and

groundwater geochemistry as previously reported by AECOM and are considered to

represent natural background concentrations, see Section 9.4 for further detail.

Dissolved sodium concentrations were detected above the screening criteria at three well

locations (WOP BH02/17, WOP BH06/17). Concentrations are only slightly elevated and

the potential risk to groundwater is therefore considered low.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


40

Sulphate was detected above the screening criteria (187.5ug/l) in 3 wells (WOP BH04/17,

WOP BH05/17, WOP-PS-GW2) with concentrations ranging between 191ug/l and

310.9ug/l. Sulphate concentrations are only slightly elevated above the screening criteria

and therefore the potential risk to groundwater is low.

Ammoniacal Nitrogen (N) concentrations range 0.04mg/l and 21.29mg/l above the

screening criteria (0.175mg/l) in all 7 samples tested at the station. Similar concentrations

were recorded at the ADF as well as at Lanesborough Power Station and associated ADF

also sent in peat environment. Given the general ranges detected across in similar peat

locations, this indicates natural background levels (associated with decaying peat

material) are elevated in this environment.

Table 10-4: 2017 ADF Groundwater Monitoring Results

Sample ID GW Regulations Screening Criteria

WOP_ADF

BH01/17

WOP_ADF

BH02/17

WOP-ADF

BH03/17

WOP ADF GW3

WOP ADF GW4

WOP ADF GW5

WOP ADF GW6


10/05/2017

10/05/2017

10/05/2017

10/05/2017

10/05/2017

10/05/2017

Parameters GTV IGV

Dissolved Arsenic

7.5 ug/l 3 19.8 19.1 2.5 2.5 49.5 14.1

Total Dissolved Iron #

200 ug/l 2602 3615 2803 1203 2691 9159 5720

Dissolved Manganese #

50 ug/l 3672 877 168 86 95 56 110

Dissolved Nickel 15 mg/l 2 15 6 2 2 20 2

Ammoniacal Nitrogen as N #

0.175 mg/l

2.07 9.22 7.52 2.03 3.17 7.95 4.71

Similar to groundwater monitoring results reported by AECOM in 2015, Arsenic

concentrations in groundwater at the ADF were detected above the GTV screening

criteria (7.5ug/l) in 4 of the 7 samples analysed. Concentrations ranged between 35ug/l

and 49.5ug/l. AECOM reported in their The Risk Screening and Technical Assessment

Report that the source of the elevated arsenic concentration is unclear but it may be

associated with elevated background concentrations often associated with the regional

geology in the area (impure limestones); or the ash landfilled at the site. Further testing of

ash leachate, undertaken by AECOM and reported in their ESB WOP Further

Assessment report, 2015, determined that arsenic was not a significant leachate from the

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


41

ash material. Consequently, the source of the arsenic is considered to be natural and the

potential environmental risk to groundwater is low.

Iron concentrations were found to be elevated in all 7 wells with concentrations ranging

between 1203ug/l and 9159ug/l. It has been previously been assessed and reported by

AECOM that there are elevated natural background levels of Iron associated with

overburden and bedrock chemistry in the area, see Section 9.4 above. Consequently, the

potential risk to the underlying groundwater is considered low given the environmental site

setting and the naturally elevated background concentrations.

All seven groundwater samples had manganese concentrations above the screening

criteria (50μg/l) with concentrations ranging from 56μg/l to 3672μg/l. Elevated manganese

concentrations are also thought to relate to bedrock and groundwater geochemistry as

previously reported by AECOM and are considered to represent natural background

concentrations.

Dissolved Nickel concentrations (20mg/l) were detected above the screening criteria

(15mg/l) at one well location (WOP ADF GW5). Concentrations are only slightly elevated

and the potential risk to groundwater is therefore considered low.

Ammoniacal Nitrogen (N) concentrations range 2.03mg/l and 9.22mg/l above the GTV of

0.175ug/l in all 7 samples tested at the station. Similar concentrations were recorded at

the ADF as well as at Lanesborough Power Station and associated ADF also set in peat

environment. Given the general ranges detected across in similar peat locations, this

indicates natural background levels are elevated in this environment.

10.4 Groundwater Monitoring Result 2014 -2017- AER Review

A review of the most recent groundwater monitoring data collected as part of the annual

monitoring program, has been undertaken for the purpose of this Baseline Report. Annual

sampling results are collated for the period 2014 to 2017. Monthly and/or quarterly

monitoring are collated for the most recent available results i.e. 2017.

All results for the period 2014 -2017 are contained within the AERs in the following

attachments to this IE Licence review:

Attachment-7-1-3-1_AER 2014


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


42



The IE Licence monitoring requirements in relation to the two monitoring boreholes at the

WOP station site are detailed below.

Table 10-5: Licence requirements: GW1 – GW6 inclusive

Parameter Requirements Frequency Analysis Method/Technique

Visual inspection/odour Quarterly NA

Groundwater Levels Quarterly NA

Total Ammonia Annually Standard Method

Total Nitrogen Annually Standard Method

COD Annually Standard Method

Hydrocarbons Quarterly Standard Method

Chloride Quarterly Standard Method

Sulphate Quarterly Standard Method

Metals/non-metals Annually Standard Method

Nitrate Annually Standard Method

Otho-Phosphate (as P) Annually Standard Method

Mercury Annually Standard Method

Electrical Conductivity Monthly Standard Method

pH Monthly pH electrode and recorder

A summary of the components discussed in the following chapters is seen in Table 10-6:.

Table 10-6:Components and their abbreviations

bbreviation Component Abbreviation Component

Al Aluminium Mn Manganese

As Arsenic Mo Molybdenum

B Boron N Nitrogen

BOD Biological Oxygen Demand Na Sodium

Ca Calcium NH4 Ammonium

Cd Cadmium Ni Nickel

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


43

bbreviation Component Abbreviation Component

COD Chemical Oxygen Demand Pb Lead

Cr Chromium PO4 Phosphate

Cu Copper Se Selenium

Fe Iron SO4 Sulphate

Hg Mercury TPH Total Petroleum

Hydrocarbons

K Potassium Zn Zinc

Mg Magnesium

10.4.1 Station – PS - GW1

Table 10-7 outlines the monitoring result in relation to PS-GW1 for the period 2014-2017

(Annual Sampling) for Total Nitrogen, Ammonia, COD and Phosphorus and Nitrates. The

majority of the annual results are generally below their respective GTVs where these

screening criteria are available. Nitrate concentrations were slightly elevated in 2015,

however concentrations were below the lower limit of detections in subsequent years.

Table 10-7: PS-GW1_ 2014-2017 (Annual Sampling Results)

Year Total Nitrogen

(mg/l)

Ammoniacal Nitrogen

as NH4 (mg/l)

COD (mg/l)

P04 (mg/l)

Nitrates (mg/l)

GTV 0.175 0.375

2014 1 <0.2 13.9 0.05 0.343

2015 <1 <0.2 18.4 0.06 0.45

2016 <1 <0.2 <7 0.02 <0.3

2017 <1 <0.2 <7 0.05 <0.3

Table 10-8 and Table 10-9 outline the monitoring results in relation to PS-GW1 for the

monthly and quarterly 2017 sampling. In 2017 for PS-GW1, the conductivity, pH

monitoring, chloride, Total Petroleum Hydrocarbons (TPH) and Sulphate (SO4) results

are consistently below the either their respective screening criteria or the lowest

laboratory limit of detection (LOD) where available.

Table 10-8: PS-GW1_ 2017 (Monthly Sampling)

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


44

Month pH Conductivity

GTV 1875 (µs/cm)

January 7.3 793

February 7.27 771

March 7.5 877

April 7.4 829

May 7.6 899

June 7.4 749

July 7.4 706

August 7.3 784

September 7.59 728

October 7.2 736

November 7.3 724

December 7.65 759

Table 10-9: PS-GW1_ 2017 (Quarterly Sampling)

Chloride TPH SO4

Units mg/l mg/l mg/l

GTV 187.5 0.075 187.5

Q1 31.4 <1 61.4

Q2 14.2 <1 41.2

Q3 14.1 <1 45.1

Q4 12.9 <1 44.5

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35

45

Table 10-10: PS-GW1_ 2014-2017 (Annual Sampling) Metals

Where GTVs or IGV are available for metals, the results are consistently below their respective screening criteria (GTV/IGV) indicating the

potential risk to groundwater is low.

Ca K Na Mg Fe Al As Cd Cu Mo Ni Se Zn B Cr Pb Mn Hg

Units (mg/l) (µg/l)

GTV 150 150 7.5 3.75 1500 15 750 37.5 18.75 0.75

IGV 200 5 50 0.2 100 50

2014 133 1.28 19.4 11.7 <0.019

<2.9 0.615

<0.1 2.54 0.757 <0.15 0.39 2.1 9.4 6.89 0.105 0.483 <0.01

2015 124 <1 14.4 11.9 <0.019

<2.9 0.537

<0.1 <0.85 0.757 2.17 2.04 3.25 16.5 0.719 <0.02 6.06 <0.01

2016 142 <1 16.9 13.7 <0.019

<2.9 0.193

0.1 1.06 0.978 2.41 0.39 3.73 15 2.29 <0.02 8.16 <0.01

2017 163 <1 10 15 0.019 <2 0.815

<0.08 <0.3 3.34 3.37 <0.5 <1 26.4 <1 <0.2 7.56 <0.01

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35

46

10.4.2 Station – PS - GW2

PSGW-2 is located outside the boundary of the station in the old Shannonbridge ash

pond and operated under the surrendered IPC Licence 626- outside the IEL boundary of

P0611-02. An exit audit for the ash pond was submitted and accepted by the EPA.

Table 10-11 outlines the annual monitoring result in relation to PS-GW2 for the period

2014-2017 for Total Nitrogen, Ammonia, COD and Phosphorus and Nitrates.

Table 10-11: PS-GW2_ 2014-2017 (Annual Sampling Results)

Year Total Nitrogen

(mg/l)

Ammoniacal Nitrogen

as NH4 (mg/l)

COD (mg/l) P04 (mg/l)

Nitrates (mg/l)

GTV 0.175 0.375

2014 6.42 6.3 14.6 0.314 < 0.3

2015 8.58 1.79 19.1 1.11 0.0842

2016 6.38 4.83 12.7 0.02 0.3

2017 6.79 6.28 17.2 0.35 0.3

Ammoniacal Nitrogen as is elevated in all samples reported between 2014 and 2017

ranging between 1.79mg/l and 6.28mg/l. As detailed in Section 11.3, similar

concentrations were recorded at the Station as well as at Lanesborough Power Station

and associated ADF also set in peat environment. Given the general ranges detected

across in similar peat locations, this indicates natural background levels are elevated in

this environment.

Table 10-12 and Table 10-13 outline the 2017 monthly and quarterly sampling monitoring

results in relation to PS-GW2. During the 2017 groundwater monitoring undertaken at PS-

GW2 the conductivity, pH monitoring, chloride, Total Petroleum Hydrocarbons analytical

results are consistently below the GTV, consequently the potential environmental risk to

groundwater is low.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


47

Table 10-12: PS-GW2_ 2017 (Monthly Sampling)

Month pH Conductivity (µs/cm)

GTV 1875

January 7.6 1193

February 7.42 1140

March 7.5 1152

April 7.4 1095

May 7.4 1015

June 7.6 1011

July 7.5 926

August 7.3 1136

September 7.75 946

October 7.5 945

November 7.5 930

December 7.78 961

Table 10-13: PS-GW2_ 2017 (Quarterly Sampling)

Chloride (mg/l)

TPH (mg/l) SO4 (mg/l)

GTV 187.5 0.075 187.5

Q1 52.4 <1 205

Q2 52.9 <1 240

Q3 53.8 <1 161

Q4 51.4 <1 166

Sulphate has exceeded the GTV on two occasions in 2017, see Table 10-13. The

concentrations are only slightly exceeding the screening criteria and consequently the

potential risk to groundwater is low. Where GTVs/IGV screening criteria are available for

metals, the results are consistently below with the exception of potassium and

Manganese.

Similar too concentrations recorded at the station, manganese concentrations were

reported above the screening criteria (50μg/l) at PS-GW2. Elevated concentrations range

from 314μg/l to 550μg/l. Elevated manganese concentrations are related to bedrock and


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


48

represent natural background concentrations. Consequently the potential risk to

groundwater is low.

Potassium concentrations ranging between 24.9ug/l and 27.6ug/l were reported between

2014 and 2017 at PS-GW2. Although the reported concentrations are above the

screening criteria (5mg/l) they are associated with natural background levels (WOP EIS

2001). Consequently they are not considered significant and the potential risk to

groundwater is low.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35

49




GTV 150 150 7.5 3.75 1500 15 750 37.5 0.75

IGV 200 5 50 0.2 100 50

2014 92 24.9 127 27.4 <0.019

<2.9 2.27 <0.1 1.83 0.777 0.15 3.4 3.48 13.3 5.71 0.047 550 <0.01

2015 105 27.6 100 22.1 0.0282

5.3 1.18 <0.1 0.886 <0.24 1.25 5.03 2.48 70 2.21 0.075 324 <0.01

2016 144 <1 17.3 13.6 <0.019

8.07 0.553 <0.1 1.04 1.3 2.6 1.41 5.08 20.6 3.43 0.02 3.99 <0.01

2017 98.9 20.4 80.7 23.8 0.05 3.03 0.5 0.08 0.3 0.88 0.4 0.5 <1 71.5 <1 0.2 314 0.01

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35

50

10.4.3 ADF - GW3

Table 10-15 outlines the monitoring result in relation to ADF-GW3 for the period 2014-

2017 (Annual Sampling) for Total Nitrogen, Ammonia, COD and Phosphorus and Nitrates.

Total Nitrogen and Phosphorus.

Table 10-15: ADF-GW3_ 2014-2017 (Annual Sampling Results)

Year Total Nitrogen

(mg/l)

Ammoniacal Nitrogen as NH4 (mg/l)

COD (mg/l)

P04 (mg/l)

Nitrates (mg/l)

GTV 0.175 0.375

2014 1.03 0.262 67.4 <0.05 <0.3

2015 1.28 0.239 67.4 <0.05 0.213

2016 <1 0.745 61.5 <0.02*7 <0.3

2017 <1 <0.2 58.9 <0.05 <0.3

*Limited of detection changed in 2016 from <0.05 to <0.02 mg/l

Ammoniacal Nitrogen concentrations for all samples are above the GTV (0.175mg/l),

albeit marginal in exceedance. Concentrations range between 0.2mg/l and 0.745mg/l.

Ammoniacal Nitrogen concentrations are attributed to elevated natural background levels

and the potential risk to underlying groundwater is considered low as a result.

Table 10-16 and

Table 10-17 outlines the 2017 monthly and quarterly sampling monitoring results in

relation to ADF-GW3. The 2017 PS-GW3 analytical results for electrical conductivity, pH,

chloride, TPH and Sulphate are consistently below the GTVs.

Table 10-16: ADF-GW3_ 2017 (Monthly Sampling)


GTV 1875

January 7.1 422

February 7.41 388

March 7.3 482

April 7.3 451

May 7.3 456

June 7.1 520

July 7.3 398

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:35


51


August 7 338

September 7.64 289

October 7.1 382

November 7 383

December 7.6 382

Table 10-17: ADF-GW3_ 2017 (Quarterly Sampling)

Chloride (mg/l)

TPH (mg/l) SO4 (mg/l)

GTV 187.5 0.075 187.5

Q1 13.3 <1 2

Q2 14.4 <1 2

Q3 8.1 <1 2

Q4 9.7 <1 2

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36

52


Where GTVs/IGV are available for metals, the results are consistently below the GTV with the exception of iron and manganese when

compared to the IGVs.

Iron concentrations exceeding its screening criteria (IGV) of 0.2mg/l range between 0.14mg/l and 0.702mg/l. Manganese concentrations

exceeding its screening criteria (50ug/l) range between 58.3ug/l and 83.5ug/l. Elevated Iron and Manganese concentrations are attributed to

natural background levels and are considered to pose a low potential risk to groundwater.

8 LOD for Selenium in 2017 was <0.5 ug/l 9 LOD for Boron in 2017 was <5 ug/l



GTV 150 150 7.5 3.75 1500 15 750 37.5 18.75 0.75

IGV 200 5 50 0.2 100 50

2014 71 1.84 10.3 5.35 0.345

9.82 1.44 0.109 2.51 0.284 0.493 <0.39 16.2

9.4 4.41 0.593 58.3 <0.01

2015 49.4 <1 8.23 4.97 0.146

14.9 0.225 0.1 0.954 0.24 0.941 <0.39 23 <9.4 1.16 0.11 2.43 <0.01

2016 83.9 <1 7.2 4.97 0.702

9.72 0.396 0.1 0.85 0.77 1.7 <0.39 3.28

<9.4 1.64 0.021 83.5 <0.01

2017 84.2 <1 6.02 5.36 0.34 16.5 1.28 <0.08 0.35 <0.5 0.817 <0.58 12 <59 <1 <0.2 60.4 <0.01

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36

53

10.4.4 ADF- GW4

The 2014-2017 annual groundwater monitoring results for ADF-GW4 are presented in

Table 10-19 for Total Nitrogen, Ammoniacal Nitrogen, COD and Phosphorus and Nitrates.


Year Total Nitrogen

(mg/l)

Ammoniacal Nitrogen

as NH4 (mg/l)


Nitrates (mg/l)

GTV 0.175 0.375

2014 3.31 2.83 76.3 <0.05 0.3

2015 2.63 2.46 67.6 <0.05 <0.067710

2016 2.09 1.45 60.2 <0.0211 0.3

2017 3.23 2.67 76.8 <0.05 0.3

Consistent with other monitored locations across the site, Ammonia exceeded its GTV

each year. Concentrations range between 1.45mg/l and 2.83mg/l. Ammoniacal Nitrogen

concentrations are attributed to elevated natural background levels linked to decaying

peat.

Table 10-20 and Table 10-21 outlines the 2017 monthly and quarterly monitoring results

in relation to ADF-GW4. For PS-GW4 for 2017 the conductivity, pH monitoring, Total

Petroleum Hydrocarbons (TPH) and Sulphate (SO4) results are consistently below the

GTV.



GTV 1875

January 7.1 640

February 7.37 594

March 7.2 533

April 7.1 545

May 7.3 538

June 7.2 547

July 7.0 535

August 7.1 673

September 7.37 622

10 LOD for nitrates in 2015 was <0.0677mg/l 11 LOD for PO4 in 2016 was <0.02mg/l

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


54


GTV 1875

October 7.0 444

November 7.1 528

December 7.47 519


Chloride (mg/l)

TPH (mg/l)

SO4 (mg/l)

GTV 187.5 0.075 187.5

Q1 25 <1 2

Q2 35 <1 2

Q3 12 <1 <2

Q4 33 <1 <2

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36

55

Table 10-22: ADF-GW4_ 2014-2017 (Annual Sampling) Metals

Month Ca K Na Mg Fe Al As Cd Cu Mo Ni Se Zn B Cr Pb Mn Hg


GTV 150 150 7.5 3.75 1500 15 750 37.5 18.75 0.75

IGV 200 5 50 0.2 100 50

2014 104 26.7 50.7 3.5 0.181

2.9 5.09 <0.1 2 0.393 0.289

6.46 0.951

<9.4 6.17 0.354 96.9 <0.01

2015 93.8 11.1 32.3 3.86 0.902

8.09 1.6 <0.1 0.85 <0.24 2.39 1.23 0.99 <9.4 1.64 0.651 115 0.0103

2016 81.6 4.27 19 3.74 1.78 7.88 0.55 <0.1 0.85 <0.24 1.63 <0.39

1.44 <9.4 1.98 0.046 88.6 <0.01

2017 95.7 9.69 26.6 2.37 2.19 9.48 0.75 <0.08

<0.3 <0.5 0.664

<0.5 3.24 <5 <1 0.249 99 <0.01

Where GTVs/IGV are available for metals, the results are consistently below the GTV with the exception of potassium, iron and manganese

when compared to the IGVs

Potassium, Iron and Manganese concentrations were reported in the AER above their respective screening criteria between 2014 and 2017.

Potassium concentrations above the screening criteria (5 mg/l) range between 9.69mg/l and 26.7mg/l. Manganese concentrations above the

screening criteria (50ug/l) range between 96.9ug/l and 115ug/l. Elevated Iron concentrations above its screening criteria (0.2mg/l) range

between 0.902mg/l and 2.19mg/l. Elevated concentrations for all three parameters are attributed to natural background levels and are

considered to pose a low potential risk to groundwater.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36

56

10.4.5 ADF - GW5


2017 (Annual Sampling) for Total Nitrogen, Ammonia, COD and Phosphorus and Nitrates.


Year Total Nitrogen

(mg/l)


COD (mg/l)

P04 (mg/l)

Nitrates (mg/l)

GTV 0.175 0.375

2014 7.71 7.42 29.8 <0.05 0.461

2015 7.78 5.59 29.1 <0.05 0.329

2016 9.18 8.74 20.8 <0.0212 <0.3

2017 8.48 8.03 31.1 <0.5 <0.3

Similar to other locations, Ammoniacal Nitrogen exceeds GTV (0.175mg/l) in 2014, 2015,

2016 and 2017 with concentrations ranging between 5.59mg/l and 8.74mg/l. Nitrates

slightly exceeded its GTV (0.375ug/l) in 2014 with a reported concentration of 0.461ug/l.

Subsequent years were below the screening criteria. All other results remain below their

GTV where available.

Table 10-24 and Table 10-25 outlines the monitoring results in relation to ADF-GW5 for

the period 2017 (monthly and quarterly sampling). For all PS-GW5 results for the

conductivity, chloride, Total Petroleum Hydrocarbons (TPH) and Sulphate (SO4) results

are consistently below the GTV.



GTV 1875

January 7.1 686

February 7.05 705

March 7.6 683

April 7 703

May 7.1 639

June 7 658

July 7 638

12 LOD for PO4 in 2016 was <0.02 mg/l

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


57


August 7.1 667

September 7.5 525

October 7.0 574

November 7.1 646

December 7.56 648


Chloride (mg/l) TPH (mg/l) SO4 (mg/l)

GTV 187.5 0.075 187.5

Q1 12.5 <1 2

Q2 11.6 <1 2

Q3 34 <1 2

Q4 12 <1 2

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36

58



Units (mg/L) (µg/l)

GTV 150 150 7.5 3.75 1500 15 750 37.5 18.75 0.75

IGV 200 5 50 0.2 100 50

2014 138 2.01 10 1.84 0.019 <2.913 18.1 <0.114

1.81 5.73 15.3 <0.315

2.55 <9.4 6.87 0.076 95.1 <0.01

2015 127 1.66 9.12 1.63 <0.019

<2.9 <9.4 <2.9 <0.85 4.34 15.6 5.77 1.91 <9.4 2.25 0.09 51.8 <0.01

2016 138 2.07 9.81 1.95 <0.019

<2.9 13.3 <0.1 <0.85 3.87 21.9 <0.39

6.97 15.1 3.31 <0.02 56 <0.01

2017 138 1.83 9.43 1.98 0.59 <2 13.9 <0.08

<0.3 5.76 19.4 <0.5 1 5.86 1 0.2 53.1 <0.01

Where GTVs/IGV are available for metals, the results are consistently below the GTV with the exception of iron, arsenic, nickel and manganese

when compared to the GTVs/ IGVs.

Iron, Arsenic, Nickle and Manganese concentrations were detected above their respective screening criteria. Iron concentrations were detected

at 0.59mg/l exceeding its IGV (0.2mg/l). Arsenic concentrations ranged between 9.4mg/l and 18.1mg/l exceeding the GTV (7.5mg/l). Nickel

concentrations reported between 2014 and 2017 ranged between 15.3ug/l and 21.9ug/l exceeding its screening criteria (15ug/l). Manganese

concentrations exceed its screening criteria (50ug/l) with concentrations ranging between 51.8ug/l and 95.1ug/l. In all cases, concentrations

were only slightly exceeding their respective screening criteria. Consequently, the potential risk to groundwater is low.

13 LOD for Aluminium in 2014 was <2.9 ug/l 14 LOD for Cadmium in 2014 was <0.1 ug/l 15 LOD for Selenium in 2014 was <0.3 ug/l

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36

59

10.4.6 ADF - GW6


2017 (Annual Sampling).


Year Total Nitrogen

(mg/l)



Nitrates (mg/l)

GTV 0.175 0.375

2014 4.48 3.87 49.2 <0.05 <0.3

2015 5.22 4.36 35.1 <0.05 <0.06

2016 4.72 4.32 25.2 <0.02 <0.3

2017 4.5 4.25 33.5 <0.05 <0.3

Nitrates were below its GTV. Ammoniacal Nitrogen concentrations exceed the GTV

(0.175mg/l) with concentrations ranging between 3.87mg/l and 4.36mg/l. are above the

GTV. Ammoniacal nitrogen concentrations are attributed to natural background levels and

therefore pose a low potential risk to groundwater.

Table 10-28 and Table 10-29 outlines the monitoring results in relation to ADF-GW6 for

the period 2017 (monthly and quarterly sampling). For PS-GW3 for 2017 the conductivity,

pH, chloride, Total Petroleum Hydrocarbons (TPH) and Sulphate (SO4) results are

consistently below the GTV.



GTV 1875

January 7 629

February 7.14 639

March 7.2 597

April 7.2 632

May 7.2 603

June 7.2 593

July 7.1 665

August 7.3 673

September 7.49 537

October 7.1 505

November 7.1 562

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


60


December 7.1 482


Chloride (mg/l)

TPH (mg/l)

SO4 (mg/l)

GTV 187.5 0.075 187.5

Q1 11.2 <1 2

Q2 10.6 <1 2

Q3 10.6 <1 2

Q4 11 <1 2

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


61


Year Ca K Na Mg Fe Al As Cd Cu Mo Ni Se Zn B Cr Pb Mn Hg

Units (mg/L) (µg/l)

GTV 150 150 7.5 3.75 1500 15 N/A 750 37.5 18.75 0.75

IGV 200 5 50 0.2 100 50

2014 110 2.99 11.3 6.83 0.168 <2.9 1.93 <0.1 0.85 1.05 1.62 0.498 2.43 <9.4 4.19 0.183 242 <0.01

2015 118 2.29 9.42 5.01 0.0492

<2.9 1.26 <0.1 <0.85 3.39 1.75 <0.39 5.11 <9.4 2.52 0.16 253 0.0133

2016 110 2.49 9.51 6.42 2.89 3.12 5.03 <0.1 <0.85 2.37 2.46 <0.39 34.2 13 0.632 <0.02 242 <0.01

2017 125 1.78 8 5.39 0.199 <2 4.13 <0.08 <0.3 2.25 0.76 <0.5 1.19 7.31 <1 <0.2 128 <0.01

Where GTVs/IGV are available for metals, the results are consistently below the GTV with the exception of iron and manganese when

compared to the IGVs.

Iron concentrations (2.89mg/l) slightly exceeded its IGV screening criteria (0.2mg/l) in 2016, however subsequent monitoring results were

below the IGV. Manganese concentrations exceed its screening criteria (50ug/l) with concentrations ranging between 128ug/l and 253ug/l. In all

cases, concentrations were only slightly exceeding their respective screening criteria. Manganese concentrations are associated with elevated

natural background levels. Consequently, the potential risk to groundwater is low.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


62

10.5 Summary of Soil Site Characteristics

No major spills and/or leaks of any chemicals or oils have been reported since

development of the site. Minor events have been reported to the EPA and addressed in

agreement with them.

An area to the south of the site (the station) was identified by AECOM as a potential risk

to controlled waters, as it contains landfilled waste materials from the former power

station. As part of this additional assessment, AECOM reported the following in relation to

soil;

Asbestos Containing Material (ACMs) were present in eleven of the seventeen

test pits excavated. All ACM observed was beneath the surface and mostly in a

bound form. Lose fibrous material was also encountered at depths of between

1.0m and 2.1meters below ground level. No ACM was observed on the surface.

Given that the observed ACM was in all cased buried, that no ACM was observed

on the ground surface and that the area has since been overlain by Bord na Mona

railway tracks, the generation of airborne asbestos fibres from the subject area

was considered unlikely.

Soil samples collected during the 2017 Site Investigation at the Station and the ADF were

below their respective GAC or the laboratory LOD. This, together with the absence of any

significant visual or olfactory signs of contamination, indicate the potential risk to Human

Health is low.

10.6 Summary of Ground Water Site Characteristics

The Risk Screening and Technical Assessment Report prepared by AECOM, in 2015 and

reviewed by the EPA, identified elevated concentrations of Arsenic, Nickel, Sulphate,

Potassium and Manganese above their respective screening criteria at the Station and

the ADF.

Elevated concentrations of Sulphate, Potassium and Manganese were attributed to

elevated natural background levels with an overall low risk identified to the underlying

groundwater bodies at the Station and the ADF.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


63

AECOM reported that the sampling methodology undertaken to collect groundwater

samples may have contributed to the elevated Arsenic and Nickel concentrations

detected. Additional assessment of the ADF leachate determined that Arsenic and Nickel

concentrations were below their respective screening criteria. Overall, AECOM concluded

that elevated Arsenic and Nickel concentrations were less than 100 times the GAC and

the risk to the groundwater body is reported as low.

Further groundwater monitoring was undertaken in 2017 by ESB at the Station and the

ADF.

Elevated aluminium concentrations were detected at the Station, however the potential

risk to the underlying groundwater is low given the environmental site setting and that the

elevated concentrations are 100 less than the screening criteria for Aluminium.

Iron concentrations were found to be elevated. It has been previously been assessed and

reported by AECOM that there are elevated natural background levels of Iron associated

with overburden and bedrock chemistry in the area, see Section 9.4 above.

Consequently, the potential risk to the underlying groundwater is considered low given the

environmental site setting and the naturally elevated background concentrations.

Groundwater samples collected at the Station had manganese concentrations above the

screening criteria. Elevated manganese concentrations are also thought to relate to

bedrock and groundwater geochemistry as previously reported by AECOM and are

considered to represent natural background concentrations. The potential risk to the

underlying groundwater is therefore considered low.

Dissolved sodium concentrations at the station were detected above the screening criteria

at three well locations at the station. Concentrations are only slightly elevated and the

potential risk to groundwater is therefore considered low.

Sulphate concentrations are only slightly elevated above the screening criteria and

therefore the potential risk to groundwater is low at the station.

Ammoniacal Nitrogen concentrations were reported above the screening criteria in all

samples tested at the station. Similar concentrations were recorded at the ADF as well as

at Lanesborough Power Station and associated ADF also sent in peat environment. Given

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


64

the general ranges detected across in similar peat locations, this indicates natural

background levels (associated with decaying peat material) are elevated in this

environment.

Similar to groundwater monitoring results reported by AECOM in 2015, Arsenic

concentrations at the ADF in groundwater were detected above the screening criteria.

AECOM reported in their The Risk Screening and Technical Assessment Report that the

source of the elevated arsenic concentration is unclear but it may be associated with

elevated background concentrations often associated with the regional geology in the

area (impure limestones); or the ash landfilled at the site. Further testing of ash leachate,

undertaken by AECOM and reported in their ESB WOP Further Assessment report, 2015,

determined that arsenic was not a significant leachate from the ash material.

Consequently, the source of the arsenic is considered to be natural background levels

and the potential environmental risk to groundwater is low.

As with Iron concentrations at the Station, Iron at the ADF was found to be elevated. It

has been previously been assessed and reported by AECOM that there are elevated

natural background levels of Iron associated with overburden and bedrock chemistry in

the area. Consequently, the potential risk to the underlying groundwater is considered low

given the environmental site setting and the naturally elevated background

concentrations.

Manganese concentrations were reported above the screening criteria at the ADF.

Elevated manganese concentrations are also thought to relate to bedrock and


represent natural background concentrations. The potential risk to groundwater is

therefore considered to be low.

Dissolved Nickel concentrations at the ADF were detected above the screening criteria at

one well location. Concentrations are only slightly elevated and the potential risk to

groundwater is therefore considered low.

Ammoniacal Nitrogen concentrations detected at the ADF were above the screening

criteria. Similar concentrations were recorded at the Station as well as at Lanesborough

Power Station and associated ADF also set in peat environment. Given the general

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


65

ranges detected across in similar peat locations, this indicates natural background levels

are elevated in this environment.

Annual groundwater results collected at the Station and reported in the AER are generally

below their respective GTVs where these screening criteria are available.

No significant groundwater quality issues were identified at PS-GW1. Nitrate

concentrations were slightly elevated in 2015, however concentrations were below the

lower limit of detections in subsequent years.

PSGW-2 is located outside the boundary of the station in the old Shannonbridge ash

pond and operated under the surrendered IPC Licence 626- outside the IEL boundary of

P0611-02. An exit audit for the ash pond was submitted and accepted by the EPA.

Ammoniacal Nitrogen as is elevated in all samples reported between 2014 and 2017

ranging between 1.79mg/l and 6.28mg/l. Similar concentrations were recorded at the

Station as well as at Lanesborough Power Station and its associated ADF which is also

set in peat environment. Given the general ranges detected across in similar peat

locations, this indicates natural background levels are elevated in this environment.

Sulphate has exceeded the screening criteria at PSGW-2 on two occasions in 2017. The

concentrations are only slightly exceeding the screening criteria and consequently the


Manganese concentrations were reported above the screening criteria at PS-GW2.

Elevated manganese concentrations are related to bedrock and groundwater

geochemistry as previously reported by AECOM and are considered to represent natural

background concentrations. Consequently the potential risk to groundwater is low.

Elevated potassium concentrations were reported between 2014 and 2017 at PS-GW2.

Although the reported concentrations are above the screening criteria they are associated

with natural background levels. Consequently they are not considered significant and the


At the ADF, Ammoniacal Nitrogen concentrations for all samples are above the screening

criteria. Iron and Manganese and Potassium concentrations also exceed their respective

screening criteria. Ammoniacal Nitrogen, Iron and Manganese concentrations are

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


66

attributed to elevated natural background levels and the potential risk to underlying

groundwater is considered low as a result.

At ADF-GW5, Arsenic and Nickle concentrations were detected above their respective

screening criteria. Concentrations were only slightly exceeding their respective screening

criteria. Consequently, the potential risk to groundwater is low.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36

67

11. Stage 7: Site investigation


Stage 7 as outlined in the Commission guidance requires the following:

If there is sufficient information from Stages 1-6 to characterise the site both laterally

and vertically and to allow the baseline status in terms of quantified levels of

pollution of soil and groundwater by relevant hazardous substances to be defined,

then go directly to Stage 8. When choosing to use existing information the operator,

in providing it, and competent authority, in assessing it, need to be aware of the

uncertainty and risk associated with using such data.

11.2 Requirement for Site investigation

Baseline information is available from existing data sources, existing reports, site

investigation reports related to construction projects and the comprehensive network of

borehole monitoring locations across the site to provide an assessment of the state of the

soils and groundwater within the site. It is considered that sufficient data is available.

Therefore no further site investigation and assessment is proposed.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


68

12. Stage 8- Baseline Report

Section 9 to Section 12 of this report represents the baseline report in line with Article

22(1) of Directive 2010/75/EU for the IE licence (no.P611-02) review application for the

WOP station.

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


69

References

ESB West Offaly Power Further Environmental Assessment 2015, completed by

AECOM (November, 2015).

ESB, West Offaly Power Hydrogeological Assessment, completed by AECOM

(June, 2015).

ESB, Shannonbridge New Peat Power Station Project Environmental Impact

Statement (EIS), Volume 1, (February 2001).

ESB West Offaly Power Risk Screening and Technical Assessment (AECOM,

August, 2015).

ESB West Offaly Power Further Environmental Assessment 2015 (AECOM,

November, 2015).

SEW Proposal for Permanent Capping Works for Cell No.1, No.2, No.3 and No. 4

at West Offaly Power Ash Disposal Facility, completed by Bord Na Mona (2014-

2016)

SEW Proposal for Construction of Cell No.5 at West Offaly Power Ash Disposal

Facility, completed by Bord Na Mona (April, 2016)

Operational Plan for West Offaly Ash Disposal Facility, prepared by Bord Na Mona

(April, 2015)

Shannonbridge Generating Station Environmental Site Investigation: Site

Characterisation Report, prepared by ESBI (September, 1995)

ESB Shannonbridge Environmental Exit Audit – Ash Ponds (related to the former

ESB Power Generating Station, Shannonbridge, Co. Offaly) (ESB, 2010).

West Offaly Power Station and the Ash Disposal Facility – Site Investigation:

Factual Report and Interpretative Report (Causeway Geotech, 2017)

ESB, West Offaly Power Industrial Emissions Licence (Licence P611-02), Annual

Environmental Report (2014).





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:36


70



European Commission(EC), Directive 2010/75/EU of the European Parliament

and of the Council of 24 November 2010 on Industrial Emissions (Integrated

Pollution Prevention and Control) (EC, 2010).

European Commission, Guidance Concerning Baseline Reports under Article

22(2) of Directive 2010/75/EU (EC, 2010).

West Offaly Power Environmental Liabilities Risk Assessment (ESB, 2016).

West Offaly Power Decommissioning Management Plan (DMP) and Closure,

Restoration and Aftercare Management Plan (CRAMP) (ESB, 2016).

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

71

Appendix 1: Total Petroleum Hydrocarbons (TPH) Breakdown

GW1 EPH C10-C40

T EPH (C6-C40)

MTBE Benzene Toluene Ethylbenzene mp Xylene O-Xylene BTEX GRO EPH (C6-C10)

Units ug/l

LOD <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q3 2015 <46 <100 3 <7 <4 <5 <8 <3 <28 <10 <100

Q4 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q1 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q2 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q3 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q4 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q1 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q2 2017 <100 <100 <3 <7 <4 <5 <8 6 <28 16 <100

Q3 2017 <100 <100 <3 <7 <4 <5 <8 <3 <29 <10 <100

Q4 2017 <100 <100 <3 <7 <4 <5 <8 <3 <29 <10 <100

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


72

GW2 EPH C10-C40

T EPH (C6-C40)

MTBE Benzene Toluene Ethylbenzene mp Xylene O-Xylene BTEX GRO EPH (C6-C10) GRO C5-C12

Units ug/l

LOD <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q2 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q3 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q2 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q4 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


73

GW3 EPH C10-C40

T EPH (C6-C40)


Units ug/l

LOD <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q2 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q3 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q2 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q4 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


74

GW4 EPH C10-C40

T EPH (C6-C40)


Units ug/l

LOD <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2015 163 163 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q2 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q3 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q2 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 12 <100 <50

Q4 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 12 <100 <50

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


75

GW5 EPH C10-C40

T EPH (C6-C40)


Units ug/l

LOD <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q2 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q3 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q2 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100

Q3 2017 <100 <100 <3 <7 19 <5 12 8 39 50 <100 59

Q4 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


76

GW6 EPH C10-C40

T EPH (C6-C40)


Units ug/l

LOD <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2015 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q2 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q3 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q4 2016 <46 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 -

Q1 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q2 2017 <100 <100 <3 <7 <4 <5 <8 <3 <28 <10 <100 <50

Q3 2017 <100 <100 <3 <7 19 <5 12 8 39 50 <100 59

Q4 2017 <100 <100 <3 <7 <4 <5 <8 5 <28 13 <100 <50

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

77

Appendix 2: CSM graphical Representation

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


78

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


79

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

80

Appendix 3 Soil Analytical Results

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

DescriptionWOP ADF

Boreholes

WOP ADF

Boreholes

JE Job No. 17/4799 17/4799

J E Sample No. 1-4 5-8

Sample IDWOP-ADF

BH01/17

WOP-ADF

BH03/17

Sampled Date Time 22/02/2017 22/02/2017

Sample Type Soil Soil

Depth 2.20 4.00

Chem Group Chem Name Unit LOD Commercial #3

Aluminium mg/kg <50 No S4UL 7939 7472

Arsenic # mg/kg <0.5 640 3.9 7.3

Barium # mg/kg <1 No S4UL 51 43

Cadmium # mg/kg <0.1 190 1.2 1.2

Chromium # mg/kg <0.5 8600 24.4 33.7

Copper # mg/kg <1 68000 19 17

Iron mg/kg <20 No S4UL 12480 12070

Lead # mg/kg <5 No S4UL 15 13

Mercury #mg/kg <0.1

1100 *

58vap

(25.8) **<0.1 <0.1

Molybdenum # mg/kg <0.1 No S4UL 1.1 2

Nickel # mg/kg <0.7 980 39.3 38.5

Selenium # mg/kg <1 12000 <1 <1

Zinc # mg/kg <5 730000 86 75

Natural Moisture Content % <0.1 No S4UL 26.2 26.3

Ammoniacal Nitrogen as N mg/kg <0.6 No S4UL 10.6 -

Chloride # mg/kg <2 No S4UL 18 -

Hexavalent Chromium # mg/kg <0.3 33 <0.3 <0.3

Ortho Phosphate as PO4 mg/kg <0.3 No S4UL <0.3 -

Sulphate as SO4 (2:1 Ext) # g/l <0.0015 No S4UL 0.0248 -

Chromium III mg/kg <0.5 8600 24.4 33.7

Organic Matter % <0.2 No S4UL 1.1 -

Notes

# ISO17025 (UKAS) accredited - UK.

#2 The LQM/CIEH S4ULs for Human Health Risk Assessment - Commercial - 1% Soil Organic Matter


*inorganic mercury

**elemental mercury

vap S4ULs presented exceed the vapour saturation limit, which is presented in brackets.

sol S4ULs presented exceed the solubility saturation limit, which is presented in brackets.

Exceeds LQM/CIEH S4ULs for Commercial

Produced: Keelin Timoney

Checked: Patrick Sweeney

Approved: Anne Marie Casey

Metals

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

Description WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

WOP ADF

Trial Pits

JE Job No. 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272

J E Sample No. 1-2 3-4 5-6 7-8 11-12 15-16 17-18 21-22 23-24 25-26 27-28 31-32 33-34 35-36

Sample IDWOP-ADF

TP02/17

WOP-ADF

TP02/17

WOP-ADF

TP03/17

WOP-ADF

TP03/17

WOP-ADF

TP04/17

WOP-ADF

TP05/17

WOP-ADF

TP06/17

WOP-ADF

TP07/17

WOP-ADF

TP08/17

WOP-ADF

TP08/17

WOP-ADF

TP09/17

WOP-ADF

TP10/17

WOP-ADF

TP01/17

WOP-ADF

TP01/17

Sampled Date Time 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil

Depth 1.50 2.50 0.50 1.50 2.50 2.00 1.00 1.50 0.50 2.50 1.00 1.00 1.50 3.00


Aluminium mg/kg <50 No S4UL 212 7575 23690 9008 6804 4400 974 1352 - 1559 1393 7952 511 4662

Arsenic # mg/kg <0.5 640 #3 0.5 7.5 5.2 2.0 11.1 2.9 2.5 1.1 - 1.4 1.0 3.3 0.7 5.9

Barium # mg/kg <1 No S4UL 34 47 120 28 88 19 29 8 - 9 9 31 9 25

Cadmium # mg/kg <0.1 190 #3 <0.1 1.0 0.7 0.2 1.0 0.8 0.2 0.7 - 0.6 0.9 0.5 <0.1 0.9

Chromium # mg/kg <0.5 8600 #3 19.0 27.7 58.9 27.5 30.9 29.6 33.9 17.1 - 15.2 17.4 48.6 16.5 32.2

Copper # mg/kg <1 68000 #3 2 15 34 11 16 11 5 5 - 6 5 15 3 11

Iron mg/kg <20 No S4UL 4812 10640 16960 13320 14140 6663 6474 3045 - 5475 2574 8603 1168 8860

Lead # mg/kg <5 No S4UL <5 13 31 12 13 9 <5 5 - <5 7 11 <5 10

Mercury # mg/kg <0.11100 *#3

58vap

(25.8) **#3<0.1 <0.1 <0.1 <0.1 0.2 <0.1 <0.1 <0.1 - <0.1 <0.1 <0.1 <0.1 <0.1

Molybdenum # mg/kg <0.1 No S4UL 2.1 1.6 1.0 0.6 2.4 2.2 3.1 0.6 - 0.6 0.8 3.1 1.3 2.2

Nickel # mg/kg <0.7 980 #3 3.8 37.7 75.0 31.1 34.1 24.5 10.3 9.9 - 12.5 9.2 37.9 2.9 28.7

Selenium # mg/kg <1 12000 #3 2 <1 1 <1 2 <1 2 <1 - <1 <1 1 <1 <1

Zinc # mg/kg <5 730000 #3 <5 69 121 62 64 36 9 23 - 26 18 58 <5 48

Naphthalene # mg/kg <0.04 190 (76.4) sol - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

Acenaphthylene mg/kg <0.03 83000 (86.1) sol - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 - <0.03 <0.03

Acenaphthene # mg/kg <0.05 84000 (57) sol - <0.05 <0.05 <0.05 - - <0.05 <0.05 - - <0.05 - <0.05 <0.05

Fluorene # mg/kg <0.04 63000 (30.9) - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

Phenanthrene # mg/kg <0.03 22000 - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 - <0.03 <0.03

Anthracene # mg/kg <0.04 520000 - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

Fluoranthene # mg/kg <0.03 23000 - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 - <0.03 <0.03

Pyrene # mg/kg <0.03 54000 - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 - <0.03 <0.03

Benzo(a)anthracene # mg/kg <0.06 170 - <0.06 <0.06 <0.06 - - <0.06 <0.06 - - <0.06 - <0.06 <0.06

Chrysene # mg/kg <0.02 350 - <0.02 <0.02 <0.02 - - <0.02 <0.02 - - <0.02 - <0.02 <0.02

Benzo(bk)fluoranthene # mg/kg <0.07 No S4UL - <0.07 <0.07 <0.07 - - <0.07 <0.07 - - <0.07 - <0.07 <0.07

Benzo(a)pyrene # mg/kg <0.04 35 - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

Indeno(123cd)pyrene # mg/kg <0.04 500 - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

Dibenzo(ah)anthracene # mg/kg <0.04 3.5 - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

Benzo(ghi)perylene # mg/kg <0.04 3900 - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

Coronene mg/kg <0.04 No S4UL - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 - <0.04 <0.04

PAH 17 Total mg/kg <0.64 No S4UL - <0.64 <0.64 <0.64 - - <0.64 <0.64 - - <0.64 - <0.64 <0.64

Benzo(b)fluoranthene mg/kg <0.05 44 - <0.05 <0.05 <0.05 - - <0.05 <0.05 - - <0.05 - <0.05 <0.05

Benzo(k)fluoranthene mg/kg <0.02 1200 - <0.02 <0.02 <0.02 - - <0.02 <0.02 - - <0.02 - <0.02 <0.02

Methyl Tertiary Butyl Ether # ug/kg <2 No S4UL - - <2 <2 - - - <2 - - <2 - <2 <2

Benzene # ug/kg <3 27000 - - <3 <3 - - - <3 - - <3 - <3 <3

Toluene # ug/kg <3 56000000vap (869000) - - <3 <3 - - - <3 - - <3 - <3 <3

Ethylbenzene # ug/kg <3 5700000vap (518000) - - <3 <3 - - - <3 - - <3 - <3 <3

p/m-Xylene # ug/kg <55900000sol (576000)

/ 6200000vap (625000)- - <5 <5 - - - <5 - - <5 - <5 <5

o-Xylene # ug/kg <3 6600000sol (478000) - - <3 <3 - - - <3 - - <3 - <3 <3

Notes

# ISO17025 (UKAS) accredited - UK. Produced: Keelin Timoney

#2 The LQM/CIEH S4ULs for Human Health Risk Assessment - Commercial - 1% Soil Organic Matter Checked: Patrick Sweeney

#3 The LQM/CIEH S4ULs for Human Health Risk Assessment - Commercial - 6% Soil Organic Matter Approved: Anne Marie Casey

#4 UK Environment Agency, Soil Guideliine Values for dioxins, furans and dioxin-lie PCBs in soil - Based on 6% Soil Organic Matter

*inorganic mercury

**elemental mercury

a S4UL for >C16-C35

b S4UL for >EC21-EC35

SV Surrogate recovery outside performance criteria. This may be due to a matrix effect.




Metals

PAH MS

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

Description

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

JE Job No. 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272 17/3272

J E Sample No. 1-2 3-4 5-6 7-8 11-12 15-16 17-18 21-22 23-24 25-26 27-28 31-32 33-34 35-36

Sample IDWOP-ADF

TP02/17

WOP-ADF

TP02/17

WOP-ADF

TP03/17

WOP-ADF

TP03/17

WOP-ADF

TP04/17

WOP-ADF

TP05/17

WOP-ADF

TP06/17

WOP-ADF

TP07/17

WOP-ADF

TP08/17

WOP-ADF

TP08/17

WOP-ADF

TP09/17

WOP-ADF

TP10/17

WOP-ADF

TP01/17

WOP-ADF

TP01/17

Sampled Date Time 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil

Depth 1.50 2.50 0.50 1.50 2.50 2.00 1.00 1.50 0.50 2.50 1.00 1.00 1.50 3.00


>C5-C6 # mg/kg <0.1 3200 (304) sol - - - <0.1 - - - <0.1 - - <0.1 - - <0.1

>C6-C8 # mg/kg <0.1 7800 (144) sol - - - <0.1 - - - <0.1 - - <0.1 - - <0.1

>C8-C10 mg/kg <0.1 2000 (78) sol - - - <0.1 - - - <0.1 - - <0.1 - - <0.1

>C10-C12 # mg/kg <0.2 9700 (48) sol - - - <0.2 - - - <0.2 - - <0.2 - - <0.2

>C12-C16 # mg/kg <4 59000 (24) sol - - - <4 - - - <4 - - <4 - - <4

>C16-C21 # mg/kg <7 160000 a - - - <7 - - - <7 - - <7 - - <7

>C21-C35 # mg/kg <7 160000 a - - - <7 - - - <7 - - <7 - - <7

Total aliphatics C5-35 mg/kg <19 160000 a - - - <19 - - - <19 - - <19 - - <19

>C5-EC7 # mg/kg <0.1 26000 (1220) sol - - - <0.1 - - - <0.1 - - <0.1 - - <0.1

>EC7-EC8 # mg/kg <0.1 56000vap (869) - - - <0.1 - - - <0.1 - - <0.1 - - <0.1

>EC8-EC10 # mg/kg <0.1 3500 (613) vap - - - <0.1 - - - <0.1 - - <0.1 - - <0.1

>EC10-EC12 # mg/kg <0.2 16000 (364) sol - - - <0.2 - - - <0.2 - - <0.2 - - <0.2

>EC12-EC16 # mg/kg <4 36000 (169) sol - - - <4 - - - <4 - - <4 - - <4

>EC16-EC21 # mg/kg <7 28000 - - - <7 - - - <7 - - <7 - - <7

>EC21-EC35 # mg/kg <7 28000 - - - <7 - - - <7 - - <7 - - <7

Total aromatics C5-35 # mg/kg <19 28000 b - - - <19 - - - <19 - - <19 - - <19

Total aliphatics and aromatics(C5-35) mg/kg <38 160000 a - - - <38 - - - <38 - - <38 - - <38

Natural Moisture Content % <0.1 No S4UL 472.4 28.1 38.7 14.7 50.3 14.0 780.0 12.5 878.3 9.3 11.5 17.7 670.0 15.6

Organic Matter % <0.2 No S4UL - - - 0.5 - - - 0.2 - - - - - 1.0

Ammoniacal Nitrogen as N mg/kg <0.6 No S4UL 17.2 - - <0.6 - - - <0.6 28.4 - - - - 4.9

Chloride # mg/kg <2 No S4UL 148 - - 24 - - - 22 121 - - - - 29

Hexavalent Chromium # mg/kg <0.3 33 #3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 - <0.3 <0.3 <0.3 <0.3 <0.3

Ortho Phosphate as PO4 mg/kg <0.3 No S4UL <0.3 - - <0.3 - - - <0.3 5.6 - - - - <0.3

Sulphate as SO4 (2:1 Ext) # g/l <0.0015 No S4UL 0.0820 - - 0.0243 - - - 0.0038 0.0115 - - - - 0.0111

Chromium III mg/kg <0.5 8600 #3 19.0 27.7 58.9 27.5 30.9 29.6 33.9 17.1 - 15.2 17.4 48.6 16.5 32.2

SVOC MS 2-Chlorophenol # ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

2-Methylphenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

2-Nitrophenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

2,4-Dichlorophenol # ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

2,4-Dimethylphenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

2,4,5-Trichlorophenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

2,4,6-Trichlorophenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

4-Chloro-3-methylphenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

4-Methylphenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

4-Nitrophenol ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

Pentachlorophenol ug/kg <10 400000 - - - <10 - - - - - - - - - <10

Phenol # ug/kg <10 760000dir (31000000) - - - <10 - - - - - - - - - <10

2-Chloronaphthalene # ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

2-Methylnaphthalene # ug/kg <10 No S4UL - - - <10 - - - - - - - - - <10

Bis(2-ethylhexyl) phthalate ug/kg <100 No S4UL - - - <100 - - - - - - - - - <100

Butylbenzyl phthalate ug/kg <100 No S4UL - - - <100 - - - - - - - - - <100

Di-n-butyl phthalate ug/kg <100 No S4UL - - - <100 - - - - - - - - - <100

Di-n-Octyl phthalate ug/kg <100 No S4UL - - - <100 - - - - - - - - - <100

Diethyl phthalate ug/kg <100 No S4UL - - - <100 - - - - - - - - - <100

Dimethyl phthalate # ug/kg <100 No S4UL - - - <100 - - - - - - - - - <100

Notes





*inorganic mercury

**elemental mercury

a S4UL for >C16-C35






Phthalates

TPH CWG

Aliphatics

Aromatics

Phenols

PAHS

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

Description WOP ADF

Trial Pits

WOP ADF

Trial Pits

JE Job No. 17/3272 17/3272


Sample IDWOP-ADF

TP03/17

WOP-ADF

TP01/17



Depth 1.50 3.00


1,2-Dichlorobenzene ug/kg <10 2000000 (571000) sol <10 <10

1,2,4-Trichlorobenzene # ug/kg <10 220000 <10 <10

1,3-Dichlorobenzene ug/kg <10 30000 <10 <10

1,4-Dichlorobenzene ug/kg <10 4400000 (224000) vap <10 <10

2-Nitroaniline ug/kg <10 No S4UL <10 <10

2,4-Dinitrotoluene ug/kg <10 No S4UL <10 <10

2,6-Dinitrotoluene ug/kg <10 No S4UL <10 <10


4-Bromophenylphenylether # ug/kg <10 No S4UL <10 <10

4-Chloroaniline ug/kg <10 No S4UL <10 <10

4-Chlorophenylphenylether ug/kg <10 No S4UL <10 <10


Azobenzene ug/kg <10 No S4UL <10 <10

Bis(2-chloroethoxy)methane ug/kg <10 No S4UL <10 <10

Bis(2-chloroethyl)ether ug/kg <10 No S4UL <10 <10

Carbazole ug/kg <10 No S4UL <10 <10

Dibenzofuran # ug/kg <10 No S4UL <10 <10

Hexachlorobenzene ug/kg <10 110000 (200) vap <10 <10

Hexachlorobutadiene # ug/kg <10 31000 <10 <10

Hexachlorocyclopentadiene ug/kg <10 No S4UL <10 <10

Hexachloroethane ug/kg <10 No S4UL <10 <10

Isophorone # ug/kg <10 No S4UL <10 <10

N-nitrosodi-n-propylamine # ug/kg <10 No S4UL <10 <10

Nitrobenzene # ug/kg <10 No S4UL <10 <10

VOC MS Dichlorodifluoromethane ug/kg <2 No S4UL <2 <2

Methyl Tertiary Butyl Ether # ug/kg <2 No S4UL <2 <2

Chloromethane # ug/kg <3 No S4UL <3 <3

Vinyl Chloride ug/kg <2 59 <2 <2

Bromomethane ug/kg <1 No S4UL <1 <1

Chloroethane # ug/kg <2 No S4UL <2 <2

Trichlorofluoromethane # ug/kg <2 No S4UL <2 <2

1,1-Dichloroethene (1,1 DCE) # ug/kg <6 No S4UL <6 <6

Dichloromethane (DCM) # ug/kg <30 No S4UL <30 <30

Notes





*inorganic mercury

**elemental mercury

a S4UL for >C16-C35









Other SVOCs

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

Description

WOP

ADF Trial

Pits

WOP

ADF Trial

Pits

JE Job No. 17/3272 17/3272


Sample IDWOP-ADF

TP03/17

WOP-ADF

TP01/17



Depth 1.50 3.00


VOC MS

continuedtrans-1-2-Dichloroethene

# ug/kg <3 No S4UL <3 <3

1,1-Dichloroethane # ug/kg <3 No S4UL <3 <3

cis-1-2-Dichloroethene # ug/kg <3 No S4UL <3 <3

2,2-Dichloropropane ug/kg <4 No S4UL <4 <4

Bromochloromethane # ug/kg <3 No S4UL <3 <3

Chloroform # ug/kg <3 No S4UL <3 <3

1,1,1-Trichloroethane # ug/kg <3 660000 <3 <3

1,1-Dichloropropene # ug/kg <3 No S4UL <3 <3

Carbon tetrachloride # ug/kg <4 2900 <4 <4

1,2-Dichloroethane # ug/kg <4 670 <4 <4

Benzene # ug/kg <3 27000 <3 <3

Trichloroethene (TCE) # ug/kg <3 1200 <3 <3

1,2-Dichloropropane # ug/kg <6 No S4UL <6 <6

Dibromomethane # ug/kg <3 No S4UL <3 <3

Bromodichloromethane # ug/kg <3 No S4UL <3 <3

cis-1-3-Dichloropropene ug/kg <4 No S4UL <4 <4

Toluene # ug/kg <3 56000000

vap (869000) <3 <3

trans-1-3-Dichloropropene ug/kg <3 No S4UL <3 <3

1,1,2-Trichloroethane # ug/kg <3 No S4UL <3 <3

Tetrachloroethene (PCE) # ug/kg <3 No S4UL <3 <3

1,3-Dichloropropane # ug/kg <3 No S4UL <3 <3

Dibromochloromethane # ug/kg <3 No S4UL <3 <3

1,2-Dibromoethane # ug/kg <3 No S4UL <3 <3

Chlorobenzene # ug/kg <3 56000 <3 <3

1,1,1,2-Tetrachloroethane ug/kg <3 110000 <3 <3

Ethylbenzene # ug/kg <3 5700000v

ap (518000) <3 <3

p/m-Xylene # ug/kg <5

5900000sol (576000)

/ 6200000vap (625000)<5 <5

o-Xylene # ug/kg <3 6600000sol (478000) <3 <3

Styrene ug/kg <3 No S4UL <3 <3

Bromoform ug/kg <3 No S4UL <3 <3

Isopropylbenzene # ug/kg <3 No S4UL <3 <3

1,1,2,2-Tetrachloroethane # ug/kg <3 270000 <3 <3

Bromobenzene ug/kg <2 No S4UL <2 <2

1,2,3-Trichloropropane # ug/kg <4 No S4UL <4 <4

Propylbenzene # ug/kg <4 No S4UL <4 <4

2-Chlorotoluene ug/kg <3 No S4UL <3 <3

1,3,5-Trimethylbenzene # ug/kg <3 No S4UL <3 <3

4-Chlorotoluene ug/kg <3 No S4UL <3 <3

tert-Butylbenzene # ug/kg <5 No S4UL <5 <5

1,2,4-Trimethylbenzene # ug/kg <6 No S4UL <6 <6

sec-Butylbenzene # ug/kg <4 No S4UL <4 <4

4-Isopropyltoluene # ug/kg <4 No S4UL <4 <4

1,3-Dichlorobenzene # ug/kg <4 30000 <4 <4

1,4-Dichlorobenzene # ug/kg <4 4400000 (224000)

vap <4 <4

n-Butylbenzene # ug/kg <4 No S4UL <4 <4


sol <4 <4

1,2-Dibromo-3-chloropropane # ug/kg <4 No S4UL <4 <4


Hexachlorobutadiene ug/kg <4 31000 <4 <4

Naphthalene ug/kg <27 190000 (76400) sol <27 <27


Notes





*inorganic mercury

**elemental mercury

a S4UL for >C16-C35









For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

DescriptionWOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

JE Job No. 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/3119 17/3119 17/3119 17/3119 17/3119

J E Sample No. 1-4 5-8 9-10 11-12 15-16 17-18 19-20 21-22 23-24 25-26 13-14 27-28 1-2 3-4 5-6 7-8 9-10

Sample ID WOP TP05/17 WOP TP05/17 WOP TP04/17 WOP TP04/17 WOP TP03/17 WOP TP03/17 WOP TP02/17 WOP TP02/17 WOP TP01/17 WOP TP01/17 WOP TP04/17 WOP TP01/17 WOP TP06/17 WOP TP06/17 WOP TP07/17 WOP TP08/17 WOP TP06/17

Sampled Date Time 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 27/01/2017 27/01/2017 27/01/2017 27/01/2017 27/01/2017

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil

Depth 1.00 4.00 2.00 3.50 0.50 2.50 1.00 2.00 0.50 3.00 0.50-2.00 0.50-1.50 0.75 1.50 0.50 1.00 0.50-1.50


Aluminium mg/kg <50 No S4UL 8159 11190 3302 7675 9979 10130 7435 8023 11300 5995 - - 8293 2604 2899 2334 -

Antimony mg/kg <1 No S4UL - - - - - - - - - - <1 <1 - - - - <1

Arsenic # mg/kg <0.5 640 27.2 34.2 3.5 12.8 29.3 36.9 28.1 36.2 26.5 3.9 12.9 20.8 40.2 6.2 6.7 4.3 5.9

Barium # mg/kg <1 No S4UL 196 199 163 273 184 225 203 176 192 73 169 200 55 17 16 15 15

Cadmium # mg/kg <0.1 190 0.5 0.7 <0.1 1.3 0.8 0.8 0.7 0.9 0.7 0.3 0.5 0.6 0.2 0.3 0.4 0.4 0.3

Chromium # mg/kg <0.5 8600 13.7 16.0 8.5 18.1 17.7 14.9 17.6 21.0 22.3 14.4 25.8 15.0 22.8 18.5 22.2 22.7 88.5

Copper # mg/kg <1 68000 20 17 5 22 17 18 18 26 22 25 14 18 10 4 8 7 5

Iron mg/kg <20 No S4UL 30370 36380 7620 20370 31510 37640 31880 33190 42000 12710 - - 23900 7366 7143 5925 -

Lead # mg/kg <5 No S4UL 20 14 <5 13 17 21 13 25 11 11 14 11 71 13 13 9 11

Mercury # mg/kg <0.11100 a

58vap

(25.8) b<0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1

Molybdenum # mg/kg <0.1 No S4UL 7.0 7.4 1.3 6.8 5.3 6.7 4.9 8.6 7.3 3.9 3.0 6.4 0.8 1.5 1.3 1.9 6.1

Nickel # mg/kg <0.7 980 32.6 36.3 10.1 42.1 34.6 33.7 35.3 42.1 54.0 25.0 26.3 34.3 36.6 10.6 16.0 14.8 13.0

Selenium # mg/kg <1 12000 7 10 2 10 10 11 10 11 8 4 5 8 <1 <1 <1 <1 <1

Zinc # mg/kg <5 730000 57 57 8 46 55 59 48 89 65 18 40 41 641 159 72 74 87

Naphthalene # mg/kg <0.04 1100 (432) sol <0.04 <0.04 <0.04 <0.04 <0.04 0.14 <0.04 <0.04 <0.04 <0.04 <0.04 0.32 <0.04 <0.04 <0.04 <0.04 <0.04

Acenaphthylene mg/kg <0.03 100000 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03

Acenaphthene # mg/kg <0.05 100000 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05

Fluorene # mg/kg <0.04 71000 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

Phenanthrene # mg/kg <0.03 23000 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03

Anthracene # mg/kg <0.04 540000 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

Fluoranthene # mg/kg <0.03 23000 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03

Pyrene # mg/kg <0.03 54000 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03

Benzo(a)anthracene # mg/kg <0.06 180 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06

Chrysene # mg/kg <0.02 350 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02

Benzo(bk)fluoranthene # mg/kg <0.07 45* <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07

Benzo(a)pyrene # mg/kg <0.04 36 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

Indeno(123cd)pyrene # mg/kg <0.04 510 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

Dibenzo(ah)anthracene # mg/kg <0.04 3.6 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

Benzo(ghi)perylene # mg/kg <0.04 4000 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

Coronene mg/kg <0.04 No S4UL <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04

PAH 17 Total mg/kg <0.64 No S4UL <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64

Benzo(b)fluoranthene mg/kg <0.05 45 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05

Benzo(k)fluoranthene mg/kg <0.02 1200 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02

Benzo(j)fluoranthene mg/kg <1 No S4UL - - - - - - - - - - <1 <1 - - - - <1

Mineral Oil (C10-C40) mg/kg <30 No S4UL - - - - - - - - - - <30 <30 - - - - <30

Notes




AA x10 dilution






a inorganic mercury

b elemental mercury

c Alpha-Hexachlorocyclohexane

d Beta-Hexachlorocyclohexane

e gamma-Hexachlorocyclohexanes (including Lindane)

f phenol

g Aliphatic 16-35

h S4UL for Aliphatic EC >35-44

i S4UL for Aromatic EC >35-44

NAD - No asbestos detected

* Surrogate using Benzo(b)fluoranthene

Metals

PAH MS

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37


Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP

Trial Pits

WOP Trial

Pits

WOP Trial

Pits

JE Job No. 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/3119 17/3119 17/3119 17/3119 17/3119

J E Sample No. 1-4 5-8 9-10 11-12 15-16 17-18 19-20 21-22 23-24 25-26 13-14 27-28 1-2 3-4 5-6 7-8 9-10

Sample ID WOP TP05/17 WOP TP05/17 WOP TP04/17 WOP TP04/17 WOP TP03/17 WOP TP03/17 WOP TP02/17 WOP TP02/17 WOP TP01/17 WOP TP01/17 WOP TP04/17 WOP TP01/17 WOP TP06/17 WOP TP06/17WOP

TP07/17WOP TP08/17 WOP TP06/17



Depth 1.00 4.00 2.00 3.50 0.50 2.50 1.00 2.00 0.50 3.00 0.50-2.00 0.50-1.50 0.75 1.50 0.50 1.00 0.50-1.50


Mineral Oil (C10-C40) mg/kg <30 No S4UL - - - - - - - - - - <30 <30 - - - - <30

Methyl Tertiary Butyl Ether # ug/kg <2 No S4UL <20AA <20AA <20AA <20AA <20SV

AA <20SV

AA <20SV

AA <20SV

AA <20SV

AA <20AA <5SV

<5SV

<5SV <2 <5 <5 <5

SV

Benzene # ug/kg <3 90000 99AA <30AA <30AA <30AA <30SV

AA <30SV

AA <30SV

AA <30SV

AA <30SV

AA 70AA <5SV

<5SV

<5SV <3 <5 <5 <5

SV

Toluene # ug/kg <3180000000

vap

(4360000) <30AA <30AA <30AA <30AA <30

SVAA <30

SVAA <30

SVAA <30

SVAA <30

SVAA <30AA <5

SV<5

SV<5

SV 3 <5 <5 <5SV

Ethylbenzene # ug/kg <3 27000000vap

(2840000) <30AA <30AA <30AA <30AA <30SV

AA <30SV

AA <30SV

AA <30SV

AA <30SV

AA <30AA <5SV

<5SV

<5SV <3 <5 <5 <5

SV


sol (3170000) /

31000000vap

(3460000) <50AA <50AA 175AA <50AA <50

SVAA <50

SVAA <50

SVAA <50

SVAA <50

SVAA <50AA <5

SV<5

SV<5

SV <5 <5 <5 <5SV

o-Xylene # ug/kg <3 33000000sol

(2620000) <30AA <30AA 92AA <30AA <30SV

AA <30SV

AA <30SV

AA <30SV

AA <30SV

AA <30AA <5SV

<5SV

<5SV <3 <5 <5 <5

SV

Aldrin mg/kg <5 170 - <5 - - - - - - - - - - - - - - -

Chlordane (cis & trans) mg/kg <5 No S4UL - <5 - - - - - - - - - - - - - - -

Chlordecone mg/kg <5 No S4UL - <5 - - - - - - - - - - - - - - -

Dieldrin mg/kg <5 170 - <5 - - - - - - - - - - - - - - -

Endrin mg/kg <5 No S4UL - <5 - - - - - - - - - - - - - - -

Heptachlor mg/kg <5 No S4UL - <5 - - - - - - - - - - - - - - -

Hexabromobiphenyl (PBB 153) mg/kg <2.5 No S4UL - <2.5 - - - - - - - - - - - - - - -

Heptabromobiphenyl (PBB 180) mg/kg <2.5 No S4UL - <2.5 - - - - - - - - - - - - - - -

Bromobiphenyls (PBB 153 & 180) mg/kg <5 No S4UL - <5 - - - - - - - - - - - - - - -

Hexachlorobenzene mg/kg <5 120 - <5 - - - - - - - - - - - - - - -

Hexachlorocyclohexane (all isomers) mg/kg <5

180 c

65 d

70 e - <5 - - - - - - - - - - - - - - -

Mirex mg/kg <5 No S4UL - <5 - - - - - - - - - - - - - - -

p,p'-DDT mg/kg <5 No S4UL - <5 - - - - - - - - - - - - - - -

Pentachlorobenzene mg/kg <5 830 - <5 - - - - - - - - - - - - - - -

PCB 28 # ug/kg <5 240

#4 - <5 - - - - - <5 - - <5 <5 - <5 - - <5

PCB 52 # ug/kg <5 240

#4 - <5 - - - - - <5 - - <5 <5 - <5 - - <5

PCB 101 # ug/kg <5 240

#4 - <5 - - - - - <5 - - <5 <5 - <5 - - <5

PCB 118 # ug/kg <5 240

#4 - <5 - - - - - <5 - - <5 <5 - <5 - - <5

PCB 138 # ug/kg <5 240

#4 - <5 - - - - - <5 - - <5 <5 - <5 - - <5

PCB 153 # ug/kg <5 240

#4 - <5 - - - - - <5 - - <5 <5 - <5 - - <5

PCB 180 # ug/kg <5 240

#4 - <5 - - - - - <5 - - <5 <5 - <5 - - <5

Total 7 PCBs # ug/kg <35 240

#4 - <35 - - - - - <35 - - <35 <35 - <35 - - <35

Notes




AA x10 dilution






a inorganic mercury

b elemental mercury




f phenol

g Aliphatic 16-35





PCBs

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:37

DescriptionWOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

WOP

Trial Pits

JE Job No. 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/3119 17/3119 17/3119 17/3119 17/3119

J E Sample No. 1-4 5-8 9-10 11-12 15-16 17-18 19-20 21-22 23-24 25-26 13-14 27-28 1-2 3-4 5-6 7-8 9-10

Sample ID WOP TP05/17 WOP TP05/17 WOP TP04/17 WOP TP04/17 WOP TP03/17 WOP TP03/17 WOP TP02/17 WOP TP02/17 WOP TP01/17 WOP TP01/17 WOP TP04/17 WOP TP01/17 WOP TP06/17 WOP TP06/17 WOP TP07/17 WOP TP08/17 WOP TP06/17



Depth 1.00 4.00 2.00 3.50 0.50 2.50 1.00 2.00 0.50 3.00 0.50-2.00 0.50-1.50 0.75 1.50 0.50 1.00 0.50-1.50


Total Phenols HPLC mg/kg <0.15 3200dir (37000) f - <0.15 - - - - - <0.15 - - - - - 0.38 - - -

Natural Moisture Content % <0.1 No S4UL 45.5 104.7 124.2 144.6 100.0 126.8 132.7 84.1 91.6 83.6 144.9 125.0 5.2 5.5 5.6 6.5 5.9

Ammoniacal Nitrogen as N mg/kg <0.6 No S4UL - <0.6 - <0.6 <0.6 <0.6 - <0.6 - <0.6 - - <0.6 3.3 <0.6 - -

Chloride # mg/kg <2 No S4UL 42 67 81 185 2480 80 - 44 - 48 - - 52 50 21 - -

Hexavalent Chromium # mg/kg <0.3 33 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3

Ortho Phosphate as PO4 mg/kg <0.3 No S4UL - <0.3 - <0.3 <0.3 <0.3 - <0.3 - <0.3 - - <0.3 <0.3 <0.3 - -

Sulphate as SO4 (2:1 Ext) # g/l <0.0015 No S4UL - 0.9992 - 0.4972 2.7156 1.8604 - 0.0471 - 0.0244 - - 0.9224 0.1850 0.3027 - -

Chromium III mg/kg <0.5 8600 13.7 16.0 8.5 18.1 17.7 14.9 17.6 21.0 22.3 14.4 25.8 15.0 22.8 18.5 22.2 22.7 88.5

Organic Matter % <0.2 No S4UL - - - 13.7 - - - 5.3 - 31.1 - - - - - - -

TPH CWG >C5-C6 # mg/kg <0.1 12000 (1150)

sol - - - - - - - - - - <0.1SV

<0.1SV - - - - <0.1

SV

>C6-C8 # mg/kg <0.1 40000 (736)

sol - - - - - - - - - - <0.1SV

<0.1SV - - - - <0.1

SV

>C8-C10 mg/kg <0.1 11000 (451) vap - - - - - - - - - - <0.1

SV<0.1

SV - - - - <0.1SV

>C10-C12 # mg/kg <0.2 47000 (283)

vap - - - - - - - - - - <0.2 <0.2 - - - - <0.2

>C12-C16 # mg/kg <4 90000 (142)

sol - - - - - - - - - - <4 <4 - - - - <4

>C16-C21 # mg/kg <7 180000 g - - - - - - - - - - <7 <7 - - - - <7

>C21-C35 # mg/kg <7 180000 g - - - - - - - - - - <7 <7 - - - - <7

>C35-C40 mg/kg <7 180000 h - - - - - - - - - - <7 <7 - - - - <7

Total aliphatics C5-40 mg/kg <26 No S4UL - - - - - - - - - - <26 <26 - - - - <26

>C6-C10 mg/kg <0.1 No S4UL - - - - - - - - - - <0.1SV

<0.1SV - - - - <0.1

SV

>C10-C25 mg/kg <10 No S4UL - - - - - - - - - - <10 <10 - - - - <10

>C25-C35 mg/kg <10 No S4UL - - - - - - - - - - <10 <10 - - - - <10

>C5-EC7 # mg/kg <0.1 86000 (4710)

sol - - - - - - - - - - <0.1SV

<0.1SV - - - - <0.1

SV

>EC7-EC8 # mg/kg <0.1 180000 (4360)

vap - - - - - - - - - - <0.1SV

<0.1SV - - - - <0.1

SV

>EC8-EC10 # mg/kg <0.1 17000 (3580)

vap - - - - - - - - - - <0.1SV

<0.1SV - - - - <0.1

SV

>EC10-EC12 # mg/kg <0.2 34000 (2150)

sol - - - - - - - - - - <0.2 <0.2 - - - - <0.2

>EC12-EC16 # mg/kg <4 38000 - - - - - - - - - - <4 <4 - - - - <4

>EC16-EC21 # mg/kg <7 28000 - - - - - - - - - - <7 <7 - - - - <7

>EC21-EC35 # mg/kg <7 28000 - - - - - - - - - - <7 <7 - - - - <7

>EC35-EC40 mg/kg <7 28000 i - - - - - - - - - - <7 <7 - - - - <7

Total aromatics C5-40 mg/kg <26 No S4UL - - - - - - - - - - <26 <26 - - - - <26

Total aliphatics and aromatics(C5-40) mg/kg <52 No S4UL - - - - - - - - - - <52 <52 - - - - <52

>EC6-EC10 # mg/kg <0.1 No S4UL - - - - - - - - - - <0.1

SV<0.1

SV - - - - <0.1SV

>EC10-EC25 mg/kg <10 No S4UL - - - - - - - - - - <10 <10 - - - - <10

>EC25-EC35 mg/kg <10 No S4UL - - - - - - - - - - <10 <10 - - - - <10

Notes




AA x10 dilution






a inorganic mercury

b elemental mercury




f phenol

g Aliphatic 16-35





Aliphatics

Aromatics

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38


Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

JE Job No. 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/2941 17/3119 17/3119 17/3119 17/3119

J E Sample No. 5-8 11-12 15-16 17-18 19-20 23-24 13-14 27-28 1-2 3-4 5-6 9-10

Sample ID WOP TP05/17 WOP TP04/17 WOP TP03/17 WOP TP03/17 WOP TP02/17 WOP TP01/17 WOP TP04/17 WOP TP01/17 WOP TP06/17 WOP TP06/17 WOP TP07/17 WOP TP06/17

Sampled Date Time 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 27/01/2017 27/01/2017 27/01/2017 27/01/2017

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil

Depth 4.00 3.50 0.50 2.50 1.00 0.50 0.50-2.00 0.50-1.50 0.75 1.50 0.50 0.50-1.50


Total Organic Carbon # % <0.02 No S4UL - - - - - - 31.39 21.79 - - - 0.44

pH # pH units <0.01 No S4UL - - - - - - 12.27 12.75 - - - 7.80

General Description (Bulk Analysis) No S4UL soil/stones soil/stones soil/stones soil/stones soil/stones soil/stones soil/stones soil/stones soil/stones - soil/stones Soil/Stones

Asbestos Fibres No S4UL NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD

Asbestos Fibres (2) No S4UL NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD

Asbestos ACM No S4UL NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD

Asbestos ACM (2) No S4UL NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD

Asbestos Type No S4UL NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD

Asbestos Type (2) No S4UL NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD

Asbestos Level Screen No S4UL NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD

2-Chlorophenol # ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

2-Methylphenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

2-Nitrophenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

2,4-Dichlorophenol # ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

2,4-Dimethylphenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

2,4,5-Trichlorophenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

2,4,6-Trichlorophenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

4-Chloro-3-methylphenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

4-Methylphenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

4-Nitrophenol ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

Pentachlorophenol ug/kg <10 400000 <10 <10 - - - - - - - <10 - -

Phenol # ug/kg <10 760000dir (31000000) <10 <10 - - - - - - - <10 - -

2-Chloronaphthalene # ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

2-Methylnaphthalene # ug/kg <10 No S4UL <10 <10 - - - - - - - <10 - -

Bis(2-ethylhexyl) phthalate ug/kg <100 No S4UL <100 <100 - - - - - - - <100 - -

Butylbenzyl phthalate ug/kg <100 No S4UL <100 <100 - - - - - - - <100 - -

Di-n-butyl phthalate ug/kg <100 No S4UL <100 <100 - - - - - - - <100 - -

Di-n-Octyl phthalate ug/kg <100 No S4UL <100 <100 - - - - - - - <100 - -

Diethyl phthalate ug/kg <100 No S4UL <100 <100 - - - - - - - <100 - -

Dimethyl phthalate # ug/kg <100 No S4UL <100 <100 - - - - - - - <100 - -

Notes




AA x10 dilution






a inorganic mercury

b elemental mercury




f phenol

g Aliphatic 16-35





Asbestos

Phenols

PAHs

Phthalates

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38


Pits

WOP Trial

Pits

WOP Trial

Pits

WOP Trial

Pits

JE Job No. 17/2941 17/2941 17/2941 17/3119

J E Sample No. 5-8 11-12 15-16 3-4

Sample ID WOP TP05/17 WOP TP04/17 WOP TP03/17 WOP TP06/17

Sampled Date Time 24/01/2017 24/01/2017 24/01/2017 27/01/2017

Sample Type Soil Soil Soil Soil

Depth 4.00 3.50 0.50 1.50


1,2-Dichlorobenzene ug/kg <10 2000000 (571000) sol <10 <10 - <10

1,2,4-Trichlorobenzene # ug/kg <10 220000 <10 <10 - <10

1,3-Dichlorobenzene ug/kg <10 30000 <10 <10 - <10

1,4-Dichlorobenzene ug/kg <10 4400000 (224000) vap <10 <10 - <10

2-Nitroaniline ug/kg <10 No S4UL <10 <10 - <10

2,4-Dinitrotoluene ug/kg <10 No S4UL <10 <10 - <10

2,6-Dinitrotoluene ug/kg <10 No S4UL <10 <10 - <10


4-Bromophenylphenylether # ug/kg <10 No S4UL <10 <10 - <10

4-Chloroaniline ug/kg <10 No S4UL <10 <10 - <10

4-Chlorophenylphenylether ug/kg <10 No S4UL <10 <10 - <10


Azobenzene ug/kg <10 No S4UL <10 <10 - <10

Bis(2-chloroethoxy)methane ug/kg <10 No S4UL <10 <10 - <10

Bis(2-chloroethyl)ether ug/kg <10 No S4UL <10 <10 - <10

Carbazole ug/kg <10 No S4UL <10 <10 - <10

Dibenzofuran # ug/kg <10 No S4UL <10 <10 - <10

Hexachlorobenzene ug/kg <10 110000 (200) vap <10 <10 - <10

Hexachlorobutadiene # ug/kg <10 31000 <10 <10 - <10

Hexachlorocyclopentadiene ug/kg <10 No S4UL <10 <10 - <10

Hexachloroethane ug/kg <10 No S4UL <10 <10 - <10

Isophorone # ug/kg <10 No S4UL <10 <10 - <10

N-nitrosodi-n-propylamine # ug/kg <10 No S4UL <10 <10 - <10

Nitrobenzene # ug/kg <10 No S4UL <10 <10 - <10

VOC MS Dichlorodifluoromethane ug/kg <2 No S4UL <20AA - <20SV

AA <2

Methyl Tertiary Butyl Ether # ug/kg <2 No S4UL <20AA - <20

SVAA <2

Chloromethane # ug/kg <3 No S4UL <30AA - <30

SVAA <3

Vinyl Chloride ug/kg <2 59 <20AA - <20SV

AA <2

Bromomethane ug/kg <1 No S4UL <10AA - <10SV

AA <1

Chloroethane # ug/kg <2 No S4UL <20AA - <20

SVAA <2

Trichlorofluoromethane # ug/kg <2 No S4UL <20AA - <20

SVAA <2

1,1-Dichloroethene (1,1 DCE) # ug/kg <6 No S4UL <60AA - <60

SVAA <6

Notes




AA x10 dilution






a inorganic mercury

b elemental mercury




f phenol

g Aliphatic 16-35








Other SVOCs

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38


Pits

WOP Trial

Pits

WOP Trial

Pits

JE Job No. 17/2941 17/2941 17/3119

J E Sample No. 5-8 15-16 3-4

Sample ID WOP TP05/17 WOP TP03/17 WOP TP06/17

Sampled Date Time 24/01/2017 24/01/2017 27/01/2017

Sample Type Soil Soil Soil

Depth 4.00 0.50 1.50


VOC MS

continuedDichloromethane (DCM)

# ug/kg <30 No S4UL <300AA <300SV

AA 45

trans-1-2-Dichloroethene # ug/kg <3 No S4UL <30AA <30

SVAA <3

1,1-Dichloroethane # ug/kg <3 No S4UL <30AA <30

SVAA <3

cis-1-2-Dichloroethene # ug/kg <3 No S4UL <30AA <30

SVAA <3

2,2-Dichloropropane ug/kg <4 No S4UL <40AA <40SV

AA <4

Bromochloromethane # ug/kg <3 No S4UL <30AA <30

SVAA <3

Chloroform # ug/kg <3 No S4UL <30AA <30

SVAA <3

1,1,1-Trichloroethane # ug/kg <3 660000 <30AA <30

SVAA <3

1,1-Dichloropropene # ug/kg <3 No S4UL <30AA <30

SVAA <3

Carbon tetrachloride # ug/kg <4 2900 <40AA <40

SVAA <4

1,2-Dichloroethane # ug/kg <4 670 <40AA <40

SVAA <4

Benzene # ug/kg <3 27000 <30AA <30

SVAA <3

Trichloroethene (TCE) # ug/kg <3 1200 <30AA <30

SVAA <3

1,2-Dichloropropane # ug/kg <6 No S4UL <60AA <60

SVAA <6

Dibromomethane # ug/kg <3 No S4UL <30AA <30

SVAA <3

Bromodichloromethane # ug/kg <3 No S4UL <30AA <30

SVAA <3

cis-1-3-Dichloropropene ug/kg <4 No S4UL <40AA <40SV

AA <4

Toluene # ug/kg <3 56000000

vap (869000) <30AA <30

SVAA 3

trans-1-3-Dichloropropene ug/kg <3 No S4UL <30AA <30SV

AA <3

1,1,2-Trichloroethane # ug/kg <3 No S4UL <30AA <30

SVAA <3

Tetrachloroethene (PCE) # ug/kg <3 No S4UL <30AA <30

SVAA <3

1,3-Dichloropropane # ug/kg <3 No S4UL <30AA <30

SVAA <3

Dibromochloromethane # ug/kg <3 No S4UL <30AA <30

SVAA <3

1,2-Dibromoethane # ug/kg <3 No S4UL <30AA <30

SVAA <3

Chlorobenzene # ug/kg <3 56000 <30AA <30

SVAA <3

1,1,1,2-Tetrachloroethane ug/kg <3 110000 <30AA <30SV

AA <3

Ethylbenzene # ug/kg <3 5700000v

ap (518000) <30AA <30

SVAA <3


5900000sol

(576000)

/ 6200000vap

(625000)<50AA <50

SVAA <5

o-Xylene # ug/kg <3 6600000sol (478000) <30AA <30

SVAA <3

Styrene ug/kg <3 No S4UL <30AA <30SV

AA <3

Bromoform ug/kg <3 No S4UL <30AA <30SV

AA <3

Isopropylbenzene # ug/kg <3 No S4UL <30AA <30

SVAA <3

1,1,2,2-Tetrachloroethane # ug/kg <3 270000 <30AA <30

SVAA <3

Bromobenzene ug/kg <2 No S4UL <20AA <20SV

AA <2

1,2,3-Trichloropropane # ug/kg <4 No S4UL <40AA <40

SVAA <4

Propylbenzene # ug/kg <4 No S4UL <40AA <40

SVAA <4

2-Chlorotoluene ug/kg <3 No S4UL <30AA <30SV

AA <3

1,3,5-Trimethylbenzene # ug/kg <3 No S4UL <30AA <30

SVAA <3

4-Chlorotoluene ug/kg <3 No S4UL <30AA <30SV

AA <3

tert-Butylbenzene # ug/kg <5 No S4UL <50AA <50

SVAA <5

1,2,4-Trimethylbenzene # ug/kg <6 No S4UL <60AA <60

SVAA <6

sec-Butylbenzene # ug/kg <4 No S4UL <40AA <40

SVAA <4

4-Isopropyltoluene # ug/kg <4 No S4UL <40AA <40

SVAA <4

1,3-Dichlorobenzene # ug/kg <4 30000 <40AA <40

SVAA <4


vap <40AA <40SV

AA <4

n-Butylbenzene # ug/kg <4 No S4UL <40AA <40

SVAA <4


sol <40AA <40SV

AA <4

1,2-Dibromo-3-chloropropane # ug/kg <4 No S4UL <40AA <40

SVAA <4

1,2,4-Trichlorobenzene # ug/kg <7 220000 <70AA <70

SVAA <7

Hexachlorobutadiene ug/kg <4 31000 <40AA <40SV

AA <4

Naphthalene ug/kg <27 190000 (76400) sol <270AA <270

SVAA <27

1,2,3-Trichlorobenzene # ug/kg <7 102000 <70AA <70

SVAA <7

Notes




AA x10 dilution






a inorganic mercury

b elemental mercury




f phenol

g Aliphatic 16-35








For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

92

Appendix 4.Soil Laboratory Results

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Unit 3 Deeside Point

Zone 3

Deeside Industrial Park

Deeside

Causeway Geotech

Attention :

Date :

Your reference :

Our reference :

Location :

Date samples received :

Status :

Issue :

Colm Hurley

28th February, 2017

1

Exova Jones Environmental

CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

8 Drumahiskey Road

Bainamore

Ballymoney

Co Antrim

BT53 7QL

Registered Address : Exova (UK) Ltd, Lochend Industrial Estate, Newbridge, Midlothian, EH28 8PL

Ten samples were received for analysis on 25th January, 2017 of which ten were scheduled for analysis. Please find attached our Test Report

which should be read with notes at the end of the report and should include all sections if reproduced. Interpretations and opinions are outside the

scope of any accreditation, and all results relate only to samples supplied.

All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.

Where Waste Acceptance Criteria Suite (EC Decision of 19 December 2002 (2003/33/EC)) has been requested, all analyses have been performed

using the relevant EN methods where they exist.

Phil Sommerton BSc

Project Manager

WOP 16-1239

Project Gemini

25th January, 2017

Final report

Compiled By:

Test Report 17/2941 Batch 1

QF-PM 3.1.1 v16Please include all sections of this report if it is reproduced

All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 16

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Client Name: Report : Solid

Reference:

Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub

Contact:

JE Job No.: 17/2941

J E Sample No. 1-4 5-8 9-10 11-12 15-16 17-18 19-20 21-22 23-24 25-26

Sample ID WOP TP05/17 WOP TP05/17 WOP TP04/17 WOP TP04/17 WOP TP03/17 WOP TP03/17 WOP TP02/17 WOP TP02/17 WOP TP01/17 WOP TP01/17

Depth 1.00 4.00 2.00 3.50 0.50 2.50 1.00 2.00 0.50 3.00

COC No / misc

Containers V J V J V J V J V J V J V J V J V J V J

Sample Date 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017

Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil

Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017

Aluminium 8159 11190 3302 7675 9979 10130 7435 8023 11300 5995 <50 mg/kg TM30/PM15

Arsenic # 27.2 34.2 3.5 12.8 29.3 36.9 28.1 36.2 26.5 3.9 <0.5 mg/kg TM30/PM15

Barium # 196 199 163 273 184 225 203 176 192 73 <1 mg/kg TM30/PM15

Cadmium # 0.5 0.7 <0.1 1.3 0.8 0.8 0.7 0.9 0.7 0.3 <0.1 mg/kg TM30/PM15

Chromium # 13.7 16.0 8.5 18.1 17.7 14.9 17.6 21.0 22.3 14.4 <0.5 mg/kg TM30/PM15

Copper # 20 17 5 22 17 18 18 26 22 25 <1 mg/kg TM30/PM15

Iron 30370 36380 7620 20370 31510 37640 31880 33190 42000 12710 <20 mg/kg TM30/PM15

Lead # 20 14 <5 13 17 21 13 25 11 11 <5 mg/kg TM30/PM15

Mercury # <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM30/PM15

Molybdenum # 7.0 7.4 1.3 6.8 5.3 6.7 4.9 8.6 7.3 3.9 <0.1 mg/kg TM30/PM15

Nickel # 32.6 36.3 10.1 42.1 34.6 33.7 35.3 42.1 54.0 25.0 <0.7 mg/kg TM30/PM15

Selenium # 7 10 2 10 10 11 10 11 8 4 <1 mg/kg TM30/PM15

Zinc # 57 57 8 46 55 59 48 89 65 18 <5 mg/kg TM30/PM15

PAH MS

Naphthalene # <0.04 <0.04 <0.04 <0.04 <0.04 0.14 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Acenaphthylene <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Acenaphthene # <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 mg/kg TM4/PM8

Fluorene # <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Phenanthrene # <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Anthracene # <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Fluoranthene # <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Pyrene # <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Benzo(a)anthracene # <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 <0.06 mg/kg TM4/PM8

Chrysene # <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 mg/kg TM4/PM8

Benzo(bk)fluoranthene # <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 <0.07 mg/kg TM4/PM8

Benzo(a)pyrene # <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Indeno(123cd)pyrene # <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Dibenzo(ah)anthracene # <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Benzo(ghi)perylene # <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Coronene <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

PAH 17 Total <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 <0.64 mg/kg TM4/PM8

Benzo(b)fluoranthene <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 mg/kg TM4/PM8

Benzo(k)fluoranthene <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 mg/kg TM4/PM8

PAH Surrogate % Recovery 109 94 48SV 109 88 78 103 107 104 88 <0 % TM4/PM8

Methyl Tertiary Butyl Ether # <20AA <20AA <20AA <20AA <20

SVAA <20

SVAA <20

SVAA <20

SVAA <20

SVAA <20AA <2 ug/kg TM15/PM10

Benzene # 99AA <30AA <30AA <30AA <30

SVAA <30

SVAA <30

SVAA <30

SVAA <30

SVAA 70AA <3 ug/kg TM15/PM10

Toluene # <30AA <30AA <30AA <30AA <30

SVAA <30

SVAA <30

SVAA <30

SVAA <30


Ethylbenzene # <30AA <30AA <30AA <30AA <30

SVAA <30

SVAA <30

SVAA <30

SVAA <30


p/m-Xylene # <50AA <50AA 175AA <50AA <50

SVAA <50

SVAA <50

SVAA <50

SVAA <50


o-Xylene # <30AA <30AA 92AA <30AA <30

SVAA <30

SVAA <30

SVAA <30

SVAA <30


Surrogate Recovery Toluene D8 88AA 74AA 73AA 75AA 81SV

AA 76SV

AA 79SV

AA 65SV

AA 71SV

AA 90AA <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 49AA 52AA 63AA 54AA 48SV

AA 47SV

AA 47SV

AA 44SV

AA 45SV

AA 57AA <0 % TM15/PM10

Project Gemini

Colm Hurley

Please see attached notes for all

abbreviations and acronyms

LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38


Reference:


Contact:

JE Job No.: 17/2941

J E Sample No. 1-4 5-8 9-10 11-12 15-16 17-18 19-20 21-22 23-24 25-26

Sample ID WOP TP05/17 WOP TP05/17 WOP TP04/17 WOP TP04/17 WOP TP03/17 WOP TP03/17 WOP TP02/17 WOP TP02/17 WOP TP01/17 WOP TP01/17

Depth 1.00 4.00 2.00 3.50 0.50 2.50 1.00 2.00 0.50 3.00

COC No / misc


Sample Date 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017 24/01/2017


Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017 25/01/2017

Aldrin - <5 - - - - - - - - <5 mg/kg TM163/PM8

Chlordane (cis & trans) - <5 - - - - - - - - <5 mg/kg TM163/PM8

Chlordecone - <5 - - - - - - - - <5 mg/kg TM163/PM8

Dieldrin - <5 - - - - - - - - <5 mg/kg TM163/PM8

Endrin - <5 - - - - - - - - <5 mg/kg TM163/PM8

Heptachlor - <5 - - - - - - - - <5 mg/kg TM163/PM8

Hexabromobiphenyl (PBB 153) - <2.5 - - - - - - - - <2.5 mg/kg TM163/PM8

Heptabromobiphenyl (PBB 180) - <2.5 - - - - - - - - <2.5 mg/kg TM163/PM8

Bromobiphenyls (PBB 153 & 180) - <5 - - - - - - - - <5 mg/kg TM163/PM8

Hexachlorobenzene - <5 - - - - - - - - <5 mg/kg TM163/PM8

Hexachlorocyclohexane (all isomers) - <5 - - - - - - - - <5 mg/kg TM163/PM8

Mirex - <5 - - - - - - - - <5 mg/kg TM163/PM8

p,p'-DDT - <5 - - - - - - - - <5 mg/kg TM163/PM8

Pentachlorobenzene - <5 - - - - - - - - <5 mg/kg TM163/PM8

PCB 28 # - <5 - - - - - <5 - - <5 ug/kg TM17/PM8

PCB 52 # - <5 - - - - - <5 - - <5 ug/kg TM17/PM8

PCB 101 # - <5 - - - - - <5 - - <5 ug/kg TM17/PM8

PCB 118 # - <5 - - - - - <5 - - <5 ug/kg TM17/PM8

PCB 138 # - <5 - - - - - <5 - - <5 ug/kg TM17/PM8

PCB 153 # - <5 - - - - - <5 - - <5 ug/kg TM17/PM8

PCB 180 # - <5 - - - - - <5 - - <5 ug/kg TM17/PM8

Total 7 PCBs # - <35 - - - - - <35 - - <35 ug/kg TM17/PM8

Total Phenols HPLC - <0.15 - - - - - <0.15 - - <0.15 mg/kg TM26/PM21

Natural Moisture Content 45.5 104.7 124.2 144.6 100.0 126.8 132.7 84.1 91.6 83.6 <0.1 % PM4/PM0

Ammoniacal Nitrogen as N - <0.6 - <0.6 <0.6 <0.6 - <0.6 - <0.6 <0.6 mg/kg TM38/PM20

Chloride # 42 67 81 185 2480 80 - 44 - 48 <2 mg/kg TM38/PM20

Hexavalent Chromium # <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 mg/kg TM38/PM20

Ortho Phosphate as PO4 - <0.3 - <0.3 <0.3 <0.3 - <0.3 - <0.3 <0.3 mg/kg TM38/PM20

Sulphate as SO4 (2:1 Ext) # - 0.9992 - 0.4972 2.7156 1.8604 - 0.0471 - 0.0244 <0.0015 g/l TM38/PM20

Chromium III 13.7 16.0 8.5 18.1 17.7 14.9 17.6 21.0 22.3 14.4 <0.5 mg/kg NONE/NONE

Organic Matter - - - 13.7 - - - 5.3 - 31.1 <0.2 % TM21/PM24

LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Client Name: Report : CEN 10:1 1 Batch

Reference:


Contact:

JE Job No.: 17/2941

J E Sample No. 5-8 11-12 15-16 21-22


Depth 4.00 3.50 0.50 2.00

COC No / misc

Containers V J V J V J V J

Sample Date 24/01/2017 24/01/2017 24/01/2017 24/01/2017


Batch Number 1 1 1 1

Date of Receipt 25/01/2017 25/01/2017 25/01/2017 25/01/2017

Dissolved Aluminium # 2.6 <1.5 186.0 6.6 <1.5 ug/l TM30/PM14

Dissolved Arsenic # 1.4 <0.9 <0.9 <0.9 <0.9 ug/l TM30/PM14

Dissolved Barium # 961.6 1169.0 35.0 196.3 <1.8 ug/l TM30/PM14

Dissolved Cadmium # <0.03 <0.03 <0.03 <0.03 <0.03 ug/l TM30/PM14

Dissolved Chromium # <0.2 <0.2 3.9 <0.2 <0.2 ug/l TM30/PM14

Dissolved Copper # <3 <3 <3 <3 <3 ug/l TM30/PM14

Dissolved Iron # <4.7 <4.7 5.1 <4.7 <4.7 ug/l TM30/PM14

Dissolved Lead # <0.4 <0.4 <0.4 <0.4 <0.4 ug/l TM30/PM14

Dissolved Mercury # 1.6 1.6 0.9 1.1 <0.5 ug/l TM30/PM14

Dissolved Molybdenum # 26.4 31.3 15.9 37.0 <0.2 ug/l TM30/PM14

Dissolved Nickel # <0.2 <0.2 <0.2 <0.2 <0.2 ug/l TM30/PM14

Dissolved Selenium # <1.2 <1.2 <1.2 <1.2 <1.2 ug/l TM30/PM14

Dissolved Zinc # 3.1 3.2 2.0 2.0 <1.5 ug/l TM30/PM14

PAH MS

Naphthalene 0.3 <0.1 0.1 <0.1 <0.1 ug/l TM4/PM30

Acenaphthylene 0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Acenaphthene 0.03 0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Fluorene 0.03 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Phenanthrene 0.04 0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Anthracene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Pyrene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(a)anthracene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Chrysene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(bk)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(a)pyrene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Indeno(123cd)pyrene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Dibenzo(ah)anthracene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(ghi)perylene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

PAH 16 Total 0.4 <0.1 0.1 <0.1 <0.1 ug/l TM4/PM30

Benzo(b)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(k)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

PAH Surrogate % Recovery 70 70 69 68 <0 % TM4/PM30

Phenol <0.5 <0.5 - <0.5 <0.5 ug/l TM26/PM0

Chloride # 8.9 27.8 - 5.9 <0.3 mg/l TM38/PM0

Ortho Phosphate as PO4 <0.03 <0.03 - <0.03 <0.03 mg/l TM38/PM0

Leachant Volume 0.802 0.753 - 0.804 l NONE/PM17

Dissolved Chromium III <2 <2 <2 <2 <2 ug/l NONE/NONE

Hexavalent Chromium <2 <2 4 <2 <2 ug/l TM38/PM0

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Client Name: SVOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 17/2941


Sample ID WOP TP05/17 WOP TP03/17

Depth 4.00 0.50

COC No / misc

Containers V J V J

Sample Date 24/01/2017 24/01/2017


Batch Number 1 1

Date of Receipt 25/01/2017 25/01/2017

SVOC MS

Phenols

2-Chlorophenol # <10 <10 <10 ug/kg TM16/PM8

2-Methylphenol <10 <10 <10 ug/kg TM16/PM8

2-Nitrophenol <10 <10 <10 ug/kg TM16/PM8

2,4-Dichlorophenol # <10 <10 <10 ug/kg TM16/PM8

2,4-Dimethylphenol <10 <10 <10 ug/kg TM16/PM8

2,4,5-Trichlorophenol <10 <10 <10 ug/kg TM16/PM8


4-Chloro-3-methylphenol <10 <10 <10 ug/kg TM16/PM8



Pentachlorophenol <10 <10 <10 ug/kg TM16/PM8

Phenol # <10 <10 <10 ug/kg TM16/PM8

PAHs

2-Chloronaphthalene # <10 <10 <10 ug/kg TM16/PM8

2-Methylnaphthalene # <10 <10 <10 ug/kg TM16/PM8

Phthalates

Bis(2-ethylhexyl) phthalate <100 <100 <100 ug/kg TM16/PM8

Butylbenzyl phthalate <100 <100 <100 ug/kg TM16/PM8

Di-n-butyl phthalate <100 <100 <100 ug/kg TM16/PM8

Di-n-Octyl phthalate <100 <100 <100 ug/kg TM16/PM8

Diethyl phthalate <100 <100 <100 ug/kg TM16/PM8

Dimethyl phthalate # <100 <100 <100 ug/kg TM16/PM8

Other SVOCs

1,2-Dichlorobenzene <10 <10 <10 ug/kg TM16/PM8

1,2,4-Trichlorobenzene # <10 <10 <10 ug/kg TM16/PM8



2-Nitroaniline <10 <10 <10 ug/kg TM16/PM8

2,4-Dinitrotoluene <10 <10 <10 ug/kg TM16/PM8



4-Bromophenylphenylether # <10 <10 <10 ug/kg TM16/PM8

4-Chloroaniline <10 <10 <10 ug/kg TM16/PM8

4-Chlorophenylphenylether <10 <10 <10 ug/kg TM16/PM8


Azobenzene <10 <10 <10 ug/kg TM16/PM8

Bis(2-chloroethoxy)methane <10 <10 <10 ug/kg TM16/PM8

Bis(2-chloroethyl)ether <10 <10 <10 ug/kg TM16/PM8

Carbazole <10 <10 <10 ug/kg TM16/PM8

Dibenzofuran # <10 <10 <10 ug/kg TM16/PM8

Hexachlorobenzene <10 <10 <10 ug/kg TM16/PM8

Hexachlorobutadiene # <10 <10 <10 ug/kg TM16/PM8

Hexachlorocyclopentadiene <10 <10 <10 ug/kg TM16/PM8

Hexachloroethane <10 <10 <10 ug/kg TM16/PM8

Isophorone # <10 <10 <10 ug/kg TM16/PM8

N-nitrosodi-n-propylamine # <10 <10 <10 ug/kg TM16/PM8

Nitrobenzene # <10 <10 <10 ug/kg TM16/PM8

Surrogate Recovery 2-Fluorobiphenyl 37 23 <0 % TM16/PM8

Surrogate Recovery p-Terphenyl-d14 56 87 <0 % TM16/PM8

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Client Name: VOC Report : Solid

Reference:

Location:

Contact:

JE Job No.: 17/2941



Depth 4.00 0.50

COC No / misc

Containers V J V J

Sample Date 24/01/2017 24/01/2017


Batch Number 1 1

Date of Receipt 25/01/2017 25/01/2017

VOC MS

Dichlorodifluoromethane <20AA <20SV

AA<2 ug/kg TM15/PM10

Methyl Tertiary Butyl Ether #

<20AA <20SV


Chloromethane #

<30AA <30SV


Vinyl Chloride <20AA <20SV

AA<2 ug/kg TM15_A/PM10

Bromomethane <10AA <10SV


Chloroethane #

<20AA <20SV


Trichlorofluoromethane #

<20AA <20SV


1,1-Dichloroethene (1,1 DCE) #

<60AA <60SV


Dichloromethane (DCM) #

<300AA <300SV


trans-1-2-Dichloroethene #

<30AA <30SV


1,1-Dichloroethane #

<30AA <30SV


cis-1-2-Dichloroethene #

<30AA <30SV


2,2-Dichloropropane <40AA <40SV


Bromochloromethane #

<30AA <30SV


Chloroform #

<30AA <30SV


1,1,1-Trichloroethane #

<30AA <30SV


1,1-Dichloropropene #

<30AA <30SV


Carbon tetrachloride #

<40AA <40SV


1,2-Dichloroethane #

<40AA <40SV


Benzene #

<30AA <30SV


Trichloroethene (TCE) #

<30AA <30SV


1,2-Dichloropropane #

<60AA <60SV


Dibromomethane #

<30AA <30SV


Bromodichloromethane #

<30AA <30SV


cis-1-3-Dichloropropene <40AA <40SV


Toluene #

<30AA <30SV


trans-1-3-Dichloropropene <30AA <30SV


1,1,2-Trichloroethane #

<30AA <30SV


Tetrachloroethene (PCE) #

<30AA <30SV


1,3-Dichloropropane #

<30AA <30SV


Dibromochloromethane #

<30AA <30SV


1,2-Dibromoethane #

<30AA <30SV


Chlorobenzene #

<30AA <30SV


1,1,1,2-Tetrachloroethane <30AA <30SV


Ethylbenzene #

<30AA <30SV


p/m-Xylene #

<50AA <50SV


o-Xylene #

<30AA <30SV


Styrene <30AA <30SV

AA<3 ug/kg TM15_A/PM10

Bromoform <30AA <30SV


Isopropylbenzene #

<30AA <30SV


1,1,2,2-Tetrachloroethane #

<30AA <30SV


Bromobenzene <20AA <20SV


1,2,3-Trichloropropane #

<40AA <40SV


Propylbenzene #

<40AA <40SV


2-Chlorotoluene <30AA <30SV


1,3,5-Trimethylbenzene #

<30AA <30SV


4-Chlorotoluene <30AA <30SV


tert-Butylbenzene #

<50AA <50SV


1,2,4-Trimethylbenzene #

<60AA <60SV


sec-Butylbenzene #

<40AA <40SV


4-Isopropyltoluene #

<40AA <40SV


1,3-Dichlorobenzene #

<40AA <40SV



<40AA <40SV


n-Butylbenzene #

<40AA <40SV



<40AA <40SV


1,2-Dibromo-3-chloropropane #

<40AA <40SV


1,2,4-Trichlorobenzene #

<70AA <70SV


Hexachlorobutadiene <40AA <40SV


Naphthalene <270AA <270SV


1,2,3-Trichlorobenzene #

<70AA <70SV


Surrogate Recovery Toluene D8 74AA 81SV

AA<0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 52AA 48SV

AA<0 % TM15/PM10

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Client Name:

Reference:

Location:

Contact:

Note:

J E

Job

No.

Batch Depth

J E

Sample

No.

Date Of

AnalysisAnalysis Result

17/2941 1 4.00 7 03/02/2017 General Description (Bulk Analysis) soil/stones

03/02/2017 Asbestos Fibres NAD

03/02/2017 Asbestos Fibres (2) NAD

03/02/2017 Asbestos ACM NAD

03/02/2017 Asbestos ACM (2) NAD

03/02/2017 Asbestos Type NAD

03/02/2017 Asbestos Type (2) NAD

03/02/2017 Asbestos Level Screen NAD

















17/2941 1 2.50 18 03/02/2017 General Description (Bulk Analysis) Soil-Silt/Stones











WOP TP02/17

WOP TP03/17

WOP TP03/17

WOP TP04/17

Ryan Butterworth

Asbestos Team Leader

Sample ID

WOP TP05/17

Analysis was carried out in accordance with our documented in-house methods PM042 and TM065 and HSG 248 by Stereo and Polarised Light Microscopy using Dispersion

Staining Techniques and is covered by our UKAS accreditation. Samples are retained for not less than 6 months from the date of analysis unless specifically requested.

Opinions, including ACM type and Asbestos level, lie outside the scope of our UKAS accreditation.

Where the sample is not taken by a Jones Environmental Laboratory consultant, Jones Environmental Laboratory cannot be responsible for inaccurate or unrepresentative

sampling.

Signed on behalf of Jones Environmental Laboratory:

Exova Jones Environmental Asbestos Analysis

Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley

QF-PM 3.1.15 v10 Please include all sections of this report if it is reproduced 7 of 16

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Asbestos Analysis

Client Name:

Reference:

Location:

Contact:

J E

Job

No.

Batch Depth

J E

Sample

No.

Date Of


17/2941 1 1.00 20 03/02/2017 Asbestos ACM NAD













WOP TP01/17

WOP TP02/17

Jones Environmental Laboratory

Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley

Sample ID


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

Notification of Deviating Samples

J E

Job

No.

Batch Depth J E Sample

No.Analysis Reason

Please note that only samples that are deviating are mentioned in this report. If no samples are listed it is because none were deviating.

Only analyses which are accredited are recorded as deviating if set criteria are not met.


WOP 16-1239

Project Gemini

Colm HurleyContact:

Sample ID

Client Name: Causeway Geotech

Reference:

Location:

No deviating sample report results for job 17/2941


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

BLANKS

NOTE

Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.

Please note we are not a UK Drinking Water Inspectorate (DWI) Approved Laboratory .

If you have not already done so, please send us a purchase order if this is required by your company.

Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable

containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and

any test results that may be compromised highlighted on your deviating samples report.

ISO17025 accreditation applies to surface water and groundwater and usually one other matrix which is analysis specific, any other liquids are

outside our scope of accreditation.

As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting samples.

Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.

Data is only reported if the laboratory is confident that the data is a true reflection of the samples analysed. Data is only reported as accredited when

all the requirements of our Quality System have been met. In certain circumstances where all the requirements of the Quality System have not been

met, for instance if the associated AQC has failed, the reason is fully investigated and documented. The sample data is then evaluated alongside

the other quality control checks performed during analysis to determine its suitability. Following this evaluation, provided the sample results have not

been effected, the data is reported but accreditation is removed. It is a UKAS requirement for data not reported as accredited to be considered

indicative only, but this does not mean the data is not valid.

Where possible, and if requested, samples will be re-extracted and a revised report issued with accredited results. Please do not hesitate to contact

the laboratory if further details are required of the circumstances which have led to the removal of accreditation.

Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our

MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations

of them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS

accredited.

Negative Neutralization Potential (NP) values are obtained when the volume of NaOH (0.1N) titrated (pH 8.3) is greater than the volume of HCl (1N)

to reduce the pH of the sample to 2.0 - 2.5. Any negative NP values are corrected to 0.

Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.

All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary.

% Asbestos in Asbestos Containing Materials (ACMs) is determined by reference to HSG 264 The Survey Guide - Appendix 2 : ACMs in buildings

listed in order of ease of fibre release.

All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless

otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.

Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to peat,

clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids. Acceptable

limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance criteria but

the associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.

A dilution suffix indicates a dilution has been performed and the reported result takes this into account. No further calculation is required.

NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS

Please note we are only MCERTS accredited (UK soils only) for sand, loam and clay and any other matrix is outside our scope of accreditation.


17/2941

WATERS

Where analytes have been found in the blank, the sample will be treated in accordance with our laboratory procedure for dealing with contaminated

blanks.

It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be

included unless we are requested to remove them.



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

JE Job No.:

#

SA

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

AA x10 Dilution

Dilution required.

Analysis subcontracted to a Jones Environmental approved laboratory.

Matrix Effect

Blank Sample

Client Sample

Trip Blank Sample

AQC Sample

Suspected carry over

Limit of Detection (Limit of Reporting) in line with ISO 17025 and MCERTS

Samples are dried at 35°C ±5°C

17/2941

AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.

Calibrated against a single substance

Not applicable

No Asbestos Detected.

No Determination Possible

Indicates analyte found in associated method blank.

None Detected (usually refers to VOC and/SVOC TICs).

ISO17025 (SANAS) accredited - South Africa.

MCERTS accredited.

Outside Calibration Range

No Fibres Detected

Result outside calibration range, results should be considered as indicative only and are not accredited.

Results expressed on as received basis.

Surrogate recovery outside performance criteria. This may be due to a matrix effect.

ISO17025 (UKAS) accredited - UK.

ABBREVIATIONS and ACRONYMS USED



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

JE Job No: 17/2941

Test Method No. Description

Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at either

35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required.


35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required. AR

TM4Modified USEPA 8270 method for the solvent extraction and determination of 16 PAHs

by GC-MS. PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex. AR Yes


by GC-MS. PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex. AR


by GC-MS. PM8

End over end extraction of solid samples for organic analysis. The solvent mix varies

depending on analysis required.AR Yes


by GC-MS. PM8


depending on analysis required.Yes AR Yes

TM5Modified USEPA 8015B method for the determination of solvent Extractable Petroleum

Hydrocarbons (EPH) with carbon banding within the range C8-C40 GC-FID. PM16 Fractionation into aliphatic and aromatic fractions using a Rapid Trace SPE. AR Yes


Hydrocarbons (EPH) with carbon banding within the range C8-C40 GC-FID. PM16 Fractionation into aliphatic and aromatic fractions using a Rapid Trace SPE. Yes AR Yes


Hydrocarbons (EPH) with carbon banding within the range C8-C40 GC-FID. PM16 Fractionation into aliphatic and aromatic fractions using a Rapid Trace SPE. AR

TM5/TM36

TM005: Modified USEPA 8015B. Determination of solvent Extractable Petroleum

Hydrocarbons (EPH) including column fractionation in the carbon range of C10-35 into

aliphatic and aromatic fractions by GC-FID.

TM036: Modified USEPA 8015B. Determination of Gasoline Range Organics (GRO) in

the carbon chain range of C5-10 by headspace GC-FID. Including determination of

BTEX and calculation of Aliphatic fractions.

PM12/PM16

Modified US EPA method 5021. Preparation of solid and liquid samples for GC

headspace analysis./Fractionation into aliphatic and aromatic fractions using a Rapid

Trace SPE.

AR Yes

Exova Jones Environmental Method Code Appendix


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

TM15Modified USEPA 8260. Quantitative Determination of Volatile Organic Compounds

(VOCs) by Headspace GC-MS.PM10


headspace analysis. AR Yes




headspace analysis. Yes AR Yes

TM16Modified USEPA 8270. Quantitative determination of Semi-Volatile Organic compounds

(SVOCs) by GC-MS. PM8







TM17Modified US EPA method 8270. Determination of specific Polychlorinated Biphenyl

congeners by GC-MS.PM8



TM20Modified BS 1377-3: 1990/USEPA 160.3 Gravimetric determination of Total Dissolved

Solids/Total SolidsPM0 No preparation is required. Yes AR Yes

TM21

Modified USEPA 415.1. Determination of Total Organic Carbon or Total Carbon by

combustion in an Eltra TOC furnace/analyser in the presence of oxygen. The CO2

generated is quantified using infra-red detection.

PM24Dried and ground solid samples are washed with hydrochloric acid, then rinsed with

deionised water to remove the mineral carbon before TOC analysis.AD Yes

TM21





deionised water to remove the mineral carbon before TOC analysis.Yes AD Yes

TM26Determination of phenols by Reversed Phased High Performance Liquid

Chromatography and Electro-Chemical Detection.PM0 No preparation is required. AR Yes


Chromatography and Electro-Chemical Detection.PM21

As received solid or water samples are extracted in Methanol: Sodium Hydroxide (0.1M

NaOH) (60:40) by orbital shaker.AR Yes



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7 and 6010BPM14

Analysis of waters and leachates for metals by ICP OES/ICP MS. Samples are filtered for

dissolved metals and acidified if required.Yes AR Yes



Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5 °C.

Samples containing asbestos are not dried and ground.AD Yes




Samples containing asbestos are not dried and ground.Yes AD Yes



Modified method EN12457-2 As received solid samples are leached with water in a 10:1

water to soil ratio for 24 hours, the moisture content of the sample is included in the ratio.Yes AR Yes

TM31Modified USEPA 8015B. Determination of Methyltertbutylether, Benzene, Toluene,

Ethylbenzene and Xylene by headspace GC-FID.PM12


headspace analysis.AR Yes




headspace analysis.Yes AR Yes

TM36Modified US EPA method 8015B. Determination of Gasoline Range Organics (GRO) in

the carbon chain range of C4-12 by headspace GC-FID. PM12







TM38Soluble Ion analysis using the Thermo Aquakem Photometric Automatic Analyser.

Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM0 No preparation is required. AR Yes


Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM0 No preparation is required. Yes AR Yes



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:38

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis


Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM20

Extraction of dried and ground or as received samples with deionised water in a 2:1

water to solid ratio using a reciprocal shaker for all analytes except hexavalent

chromium. Extraction of as received sample using 10:1 ratio of 0.2M sodium hydroxide to

soil for hexavalent chromium using a reciprocal shaker.

AD Yes







Yes AD Yes







AR Yes







Yes AR Yes

TM60

Modified USEPA 9060. Determination of TOC by calculation from Total Carbon and

Inorganic Carbon using a TOC analyser, the carbon in the sample is converted to CO2

and then passed through a non-dispersive infrared gas analyser (NDIR).

PM0 No preparation is required. AR Yes

TM61Modified US EPA methods 245.7 and 200.7. Determination of Mercury by Cold Vapour

Atomic Fluorescence. PM38

Samples are brominated to reduce all mercury compounds to Mercury (II) which is

analysed using method TM061.Yes AR Yes

TM65 Asbestos Bulk Identification method based on HSG 248. PM42Solid samples undergo a thorough visual inspection for asbestos fibres prior to asbestos

identification using TM065.AR


identification using TM065.Yes AR

TM73Modified US EPA methods 150.1 and 9045D. Determination of pH by Metrohm

automated probe analyser.PM0 No preparation is required. AR Yes


automated probe analyser.PM11 Extraction of as received solid samples using one part solid to 2.5 parts deionised water. Yes AR No



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

TM163Quantitative determination of Persistent Organic Pollutants (Pesticides) and Toxaphene

by GC-MSPM8



TM173 Analysis of fluoride by ISE (Ion Selective Electrode) using modified ISE method 340.2 PM0 No preparation is required. AR Yes

NONE No Method Code NONE No Method Code AR Yes

NONE No Method Code PM17Modified method EN12457-2 As received solid samples are leached with water in a 10:1

water to soil ratio for 24 hours, the moisture content of the sample is included in the ratio.


water to soil ratio for 24 hours, the moisture content of the sample is included in the ratio.AR

NONE No Method Code PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at either

35°C or 105°C. Calculation based on ISO 11465 and BS1377.AR

TM15_AModified USEPA 8260. Quantitative Determination of Volatile Organic Compounds, Vinyl

Chloride & Styrene by Headspace GC-MS.PM10





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39


Zone 3


Deeside

Causeway Geotech

Attention :

Date :

Your reference :

Our reference :

Location :


Status :

Issue :

Colm Hurley

28th February, 2017

1


CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

8 Drumahiskey Road

Bainamore

Ballymoney

Co Antrim

BT53 7QL


Two samples were received for analysis on 25th January, 2017 of which two were scheduled for analysis. Please find attached our Test Report






Phil Sommerton BSc

Project Manager

WOP 16-1239

Project Gemini

25th January, 2017

Final report

Compiled By:




For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39


Reference:


Contact:

JE Job No.: 17/2941

J E Sample No. 13-14 27-28


Depth 0.50-2.00 0.50-1.50

COC No / misc

Containers V J V J

Sample Date 24/01/2017 24/01/2017


Batch Number 1 1

Date of Receipt 25/01/2017 25/01/2017

Antimony <1 <1 <1 mg/kg TM30/PM15

Arsenic # 12.9 20.8 <0.5 mg/kg TM30/PM15

Barium # 169 200 <1 mg/kg TM30/PM15

Cadmium # 0.5 0.6 <0.1 mg/kg TM30/PM15

Chromium # 25.8 15.0 <0.5 mg/kg TM30/PM15

Copper # 14 18 <1 mg/kg TM30/PM15

Lead # 14 11 <5 mg/kg TM30/PM15

Mercury # <0.1 <0.1 <0.1 mg/kg TM30/PM15

Molybdenum # 3.0 6.4 <0.1 mg/kg TM30/PM15

Nickel # 26.3 34.3 <0.7 mg/kg TM30/PM15

Selenium # 5 8 <1 mg/kg TM30/PM15

Zinc # 40 41 <5 mg/kg TM30/PM15

PAH MS

Naphthalene # <0.04 0.32 <0.04 mg/kg TM4/PM8

Acenaphthylene <0.03 <0.03 <0.03 mg/kg TM4/PM8

Acenaphthene # <0.05 <0.05 <0.05 mg/kg TM4/PM8

Fluorene # <0.04 <0.04 <0.04 mg/kg TM4/PM8

Phenanthrene # <0.03 <0.03 <0.03 mg/kg TM4/PM8

Anthracene # <0.04 <0.04 <0.04 mg/kg TM4/PM8

Fluoranthene # <0.03 <0.03 <0.03 mg/kg TM4/PM8

Pyrene # <0.03 <0.03 <0.03 mg/kg TM4/PM8

Benzo(a)anthracene # <0.06 <0.06 <0.06 mg/kg TM4/PM8

Chrysene # <0.02 <0.02 <0.02 mg/kg TM4/PM8

Benzo(bk)fluoranthene # <0.07 <0.07 <0.07 mg/kg TM4/PM8

Benzo(a)pyrene # <0.04 <0.04 <0.04 mg/kg TM4/PM8

Indeno(123cd)pyrene # <0.04 <0.04 <0.04 mg/kg TM4/PM8

Dibenzo(ah)anthracene # <0.04 <0.04 <0.04 mg/kg TM4/PM8

Benzo(ghi)perylene # <0.04 <0.04 <0.04 mg/kg TM4/PM8

Coronene <0.04 <0.04 <0.04 mg/kg TM4/PM8

PAH 6 Total # <0.22 <0.22 <0.22 mg/kg TM4/PM8

PAH 17 Total <0.64 <0.64 <0.64 mg/kg TM4/PM8

Benzo(b)fluoranthene <0.05 <0.05 <0.05 mg/kg TM4/PM8

Benzo(k)fluoranthene <0.02 <0.02 <0.02 mg/kg TM4/PM8

Benzo(j)fluoranthene <1 <1 <1 mg/kg TM4/PM8

PAH Surrogate % Recovery 36 93 <0 % TM4/PM8

Mineral Oil (C10-C40) <30 <30 <30 mg/kg TM5/PM16

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39


Reference:


Contact:

JE Job No.: 17/2941

J E Sample No. 13-14 27-28


Depth 0.50-2.00 0.50-1.50

COC No / misc

Containers V J V J

Sample Date 24/01/2017 24/01/2017


Batch Number 1 1

Date of Receipt 25/01/2017 25/01/2017

TPH CWG

Aliphatics

>C5-C6 #

<0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>C6-C8 #

<0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>C8-C10 <0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>C10-C12 # <0.2 <0.2 <0.2 mg/kg TM5/PM16

>C12-C16 # <4 <4 <4 mg/kg TM5/PM16

>C16-C21 # <7 <7 <7 mg/kg TM5/PM16

>C21-C35 # <7 <7 <7 mg/kg TM5/PM16

>C35-C40 <7 <7 <7 mg/kg TM5/PM16

Total aliphatics C5-40 <26 <26 <26 mg/kg TM5/TM36/PM12/PM16

>C6-C10 <0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>C10-C25 <10 <10 <10 mg/kg TM5/PM16

>C25-C35 <10 <10 <10 mg/kg TM5/PM16

Aromatics

>C5-EC7 #

<0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>EC7-EC8 #

<0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>EC8-EC10 #

<0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>EC10-EC12 # <0.2 <0.2 <0.2 mg/kg TM5/PM16

>EC12-EC16 # <4 <4 <4 mg/kg TM5/PM16

>EC16-EC21 # <7 <7 <7 mg/kg TM5/PM16

>EC21-EC35 # <7 <7 <7 mg/kg TM5/PM16

>EC35-EC40 <7 <7 <7 mg/kg TM5/PM16

Total aromatics C5-40 <26 <26 <26 mg/kg TM5/TM36/PM12/PM16

Total aliphatics and aromatics(C5-40) <52 <52 <52 mg/kg TM5/TM36/PM12/PM16

>EC6-EC10 #

<0.1SV

<0.1SV <0.1 mg/kg TM36/PM12

>EC10-EC25 <10 <10 <10 mg/kg TM5/PM16

>EC25-EC35 <10 <10 <10 mg/kg TM5/PM16

MTBE #

<5SV

<5SV <5 ug/kg TM31/PM12

Benzene #

<5SV


Toluene #

<5SV


Ethylbenzene #

<5SV


m/p-Xylene #

<5SV


o-Xylene #

<5SV


PCB 28 # <5 <5 <5 ug/kg TM17/PM8

PCB 52 # <5 <5 <5 ug/kg TM17/PM8

PCB 101 # <5 <5 <5 ug/kg TM17/PM8

PCB 118 # <5 <5 <5 ug/kg TM17/PM8

PCB 138 # <5 <5 <5 ug/kg TM17/PM8

PCB 153 # <5 <5 <5 ug/kg TM17/PM8

PCB 180 # <5 <5 <5 ug/kg TM17/PM8

Total 7 PCBs # <35 <35 <35 ug/kg TM17/PM8

LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39


Reference:


Contact:

JE Job No.: 17/2941

J E Sample No. 13-14 27-28


Depth 0.50-2.00 0.50-1.50

COC No / misc

Containers V J V J

Sample Date 24/01/2017 24/01/2017


Batch Number 1 1

Date of Receipt 25/01/2017 25/01/2017

Natural Moisture Content 144.9 125.0 <0.1 % PM4/PM0

Moisture Content (% Wet Weight) 59.2 55.6 <0.1 % PM4/PM0

Hexavalent Chromium # <0.3 <0.3 <0.3 mg/kg TM38/PM20

Chromium III 25.8 15.0 <0.5 mg/kg NONE/NONE

Total Organic Carbon # 31.39 21.79 <0.02 % TM21/PM24

pH # 12.27 12.75 <0.01 pH units TM73/PM11

Mass of raw test portion 0.2589 0.1826 kg NONE/PM17

Mass of dried test portion 0.09 0.09 kg NONE/PM17

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39


Reference:


Contact:

JE Job No.: 17/2941

J E Sample No. 13-14 27-28


Depth 0.50-2.00 0.50-1.50

COC No / misc

Containers V J V J

Sample Date 24/01/2017 24/01/2017


Batch Number 1 1

Date of Receipt 25/01/2017 25/01/2017

Dissolved Antimony # <0.002 <0.002 <0.002 mg/l TM30/PM17

Dissolved Antimony (A10) # <0.02 <0.02 <0.02 mg/kg TM30/PM17

Dissolved Arsenic # <0.0025 <0.0025 <0.0025 mg/l TM30/PM17

Dissolved Arsenic (A10) # <0.025 <0.025 <0.025 mg/kg TM30/PM17

Dissolved Barium # 0.312 0.842 <0.003 mg/l TM30/PM17

Dissolved Barium (A10) # 3.12 8.42 <0.03 mg/kg TM30/PM17

Dissolved Cadmium # <0.0005 <0.0005 <0.0005 mg/l TM30/PM17

Dissolved Cadmium (A10) # <0.005 <0.005 <0.005 mg/kg TM30/PM17

Dissolved Chromium # <0.0015 <0.0015 <0.0015 mg/l TM30/PM17

Dissolved Chromium (A10) # <0.015 <0.015 <0.015 mg/kg TM30/PM17

Dissolved Copper # <0.007 <0.007 <0.007 mg/l TM30/PM17

Dissolved Copper (A10) # <0.07 <0.07 <0.07 mg/kg TM30/PM17

Dissolved Lead # <0.005 <0.005 <0.005 mg/l TM30/PM17

Dissolved Lead (A10) # <0.05 <0.05 <0.05 mg/kg TM30/PM17

Dissolved Molybdenum # 0.035 0.040 <0.002 mg/l TM30/PM17

Dissolved Molybdenum (A10) # 0.35 0.40 <0.02 mg/kg TM30/PM17

Dissolved Nickel # <0.002 <0.002 <0.002 mg/l TM30/PM17

Dissolved Nickel (A10) # <0.02 <0.02 <0.02 mg/kg TM30/PM17

Dissolved Selenium # <0.003 <0.003 <0.003 mg/l TM30/PM17

Dissolved Selenium (A10) # <0.03 <0.03 <0.03 mg/kg TM30/PM17

Dissolved Zinc # 0.004 0.007 <0.003 mg/l TM30/PM17

Dissolved Zinc (A10) # 0.04 0.07 <0.03 mg/kg TM30/PM17

Mercury Dissolved by CVAF # <0.00001 <0.00001 <0.00001 mg/l TM61/PM38

Mercury Dissolved by CVAF # <0.0001 <0.0001 <0.0001 mg/kg TM61/PM38

Phenol <0.01 <0.01 <0.01 mg/l TM26/PM0

Phenol <0.1 <0.1 <0.1 mg/kg TM26/PM0

Fluoride <0.3 <0.3 <0.3 mg/l TM173/PM0

Fluoride <3 <3 <3 mg/kg TM173/PM0

Sulphate # 27.90 24.15 <0.05 mg/l TM38/PM0

Sulphate # 278.9 241.4 <0.5 mg/kg TM38/PM0

Chloride # 9.7 9.1 <0.3 mg/l TM38/PM0

Chloride # 97 91 <3 mg/kg TM38/PM0

Leachant Volume 0.73 0.807 l NONE/PM17

Eluate Volume 0.53 0.05 l NONE/PM17

Dissolved Organic Carbon 5 20 <2 mg/l TM60/PM0

Dissolved Organic Carbon 50 200 <20 mg/kg TM60/PM0

pH 12.15 12.66 <0.01 pH units TM73/PM0

Total Dissolved Solids # 784 1841 <35 mg/l TM20/PM0

Total Dissolved Solids # 7836 18406 <350 mg/kg TM20/PM0

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

Mass of sample taken (kg) 0.2589 Dry Matter Content Ratio (%) = 34.7

Mass of dry sample (kg) = 0.09 Leachant Volume (l) 0.73

Particle Size <4mm = >95% Eluate Volume (l) 0.53

JEFL Job No

Sample No

Client Sample No

Depth/Other

Sample Date

Batch No

Solid Waste Analysis

Total Organic Carbon (%) 31.39 3 5 6

Sum of BTEX (mg/kg) <0.025 6 - -

Sum of 7 PCBs (mg/kg) <0.035 1 - -

Mineral Oil (mg/kg) <30 500 - -

PAH Sum of 6 (mg/kg) <0.22 - - -

PAH Sum of 17 (mg/kg) <0.64 100 - -

10:1

concn

leached

A10

mg/kg

Arsenic <0.025 0.5 2 25

Barium 3.12 20 100 300

Cadmium <0.005 0.04 1 5

Chromium <0.015 0.5 10 70

Copper <0.07 2 50 100

Mercury <0.0001 0.01 0.2 2

Molybdenum 0.35 0.5 10 30

Nickel <0.02 0.4 10 40

Lead <0.05 0.5 10 50

Antimony <0.02 0.06 0.7 5

Selenium <0.03 0.1 0.5 7

Zinc 0.04 4 50 200

Chloride 97 800 15000 25000

Fluoride <3 10 150 500

Sulphate as SO4 278.9 1000 20000 50000

Total Dissolved Solids 7836 4000 60000 100000

Phenol <0.1 1 - -

Dissolved Organic Carbon 50 500 800 1000

24/01/2017

1

Eluate Analysis

Limit values for compliance

leaching test using

BS EN 12457-2 at L/S 10 l/kg

mg/kg

Exova Jones Environmental EN-12457-2 Result Report

17/2941 Landfill Waste Acceptance

Criteria Limits 14

WOP TP04/17

InertStable

Non-reactiveHazardous

0.50-2.00



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39




JEFL Job No

Sample No

Client Sample No

Depth/Other

Sample Date

Batch No




Sum of 7 PCBs (mg/kg) <0.035 1 - -


PAH Sum of 6 (mg/kg) <0.22 - - -

PAH Sum of 17 (mg/kg) <0.64 100 - -

10:1

concn

leached

A10

mg/kg

Arsenic <0.025 0.5 2 25

Barium 8.42 20 100 300

Cadmium <0.005 0.04 1 5

Chromium <0.015 0.5 10 70

Copper <0.07 2 50 100

Mercury <0.0001 0.01 0.2 2


Nickel <0.02 0.4 10 40

Lead <0.05 0.5 10 50

Antimony <0.02 0.06 0.7 5

Selenium <0.03 0.1 0.5 7

Zinc 0.07 4 50 200

Chloride 91 800 15000 25000

Fluoride <3 10 150 500

Sulphate as SO4 241.4 1000 20000 50000


Phenol <0.1 1 - -

Dissolved Organic Carbon 200 500 800 1000

24/01/2017

1

Eluate Analysis


leaching test using

BS EN 12457-2 at L/S 10 l/kg

mg/kg



Criteria Limits 28

WOP TP01/17

InertStable


0.50-1.50



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

EPH Interpretation Report

Matrix : Solid

J E

Job

No.


No.EPH Interpretation

17/2941 1 0.50-2.00 13-14 No interpretation possible


Contact: Colm Hurley

Sample ID

WOP TP04/17

WOP TP01/17


Reference: WOP 16-1239

Location: Project Gemini



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

Client Name:

Reference:

Location:

Contact:

Note:

J E

Job

No.

Batch Depth

J E

Sample

No.

Date Of


17/2941 1 0.50-2.00 14 03/02/2017 General Description (Bulk Analysis) soil/stones








17/2941 1 0.50-1.50 28 03/02/2017 General Description (Bulk Analysis) Soil-Silt/Stones








WOP TP01/17

Ryan Butterworth


Sample ID

WOP TP04/17





sampling.



Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39


J E

Job

No.


No.Analysis Reason




WOP 16-1239

Project Gemini

Colm HurleyContact:

Sample ID


Reference:

Location:



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

BLANKS

NOTE






















accredited.

















17/2941

WATERS


blanks.





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No.:

#

SA

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

Dilution required.


Matrix Effect

Blank Sample

Client Sample

Trip Blank Sample

AQC Sample




17/2941



Not applicable






MCERTS accredited.


No Fibres Detected








For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis










by GC-MS. PM8




by GC-MS. PM8









TM5/TM36







PM12/PM16



Trace SPE.

AR Yes



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis























TM21






TM21














For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis







































For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis







AD Yes







Yes AD Yes







AR Yes







Yes AR Yes

TM60



















For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:39

JE Job No: 17/2941


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

TM163Quantitative determination of Persistent Organic Pollutants (Pesticides) and Toxaphene

by GC-MSPM8

















For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

Leachate tests

10l/kg; 4mmI.S. EN 12457-2:2002 Specified particle size; water added to L/S ratio; capped; agitated for 24 ± 0.5 hours; eluate settled and

filtered over 0.45 μm membrane filter.

Eluate analysis

As I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Ba I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Cd I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Cr total I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Cu I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Hg I.S. EN 13370 rec. EN 1483 (CVAAS)

Mo I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Ni I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Pb I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Sb I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Se I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Zn I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Chloride I.S. EN 12506 rec. EN ISO 10304-part 1 (liquid chromatography of ions)

Fluoride I.S. EN 12506 rec. EN ISO 10304-part 1 (liquid chromatography of ions)

Sulphate I.S. EN 12506 rec. EN ISO 10304-part 1 (liquid chromatography of ions)

Phenol index I.S. EN 13370 rec. ISO 6439 (4-Aminoantipyrine spectrometic methods after distillation)* ( BY HPLC - Jones Env)

DOC I.S. EN 1484

TDS I.S. EN 15216

Compositional analysis

TOC I.S. EN 13137 Method B: carbonates removed with acid; TOC by combustion.

BTEX GC-FID

PCB7** I.S. EN 15308 analysis by GC-ECD.

Mineral oil I.S. EN 14039 C10 to C40 analysis by GC-FID.

PAH17*** I.S. EN 15527 PAH17 analysis by GC-MS

Metals I.S. EN 13657 - Aqua regia digestion: EN ISO 11885 ( ICP-OES)

Other

Dry matter

I.S. EN 14346 sample is dried to a constant mass in an oven at 105 ± 3 °C; Method B Water content by direct Karl-Fischer-

titration and either volumetric or coulometric detection.

LOI I.S. EN 15169 Difference in mass after heating in a furnace up to 550 ± 25 °C.

ANC CEN/TS 15364 Determined by amouns of acid or base needed to cover the pH range

Notes:

*If not suitable due to LOD, precision, etc., any other suitable method can be used, e.g. AFS, ICP-MS

**PCB-28, PCB-52, PCB-101, PCB-118, PCB-138, PCB-153 and PCB-180

Appendix - Methods used for WAC (2003/33/EC)

***Naphthalene, Acenaphthylene, Acenaphthene, Anthracene, Benzo(a)anthracene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(g,h,i)perylene,

Benzo(a)pyrene, Chrysene, Coronene, Dibenzo(a,h)anthracene, Fluorene, Fluoranthene, Indeno(1,2,3-c,d)pyrene, Phenanthrene and Pyrene.


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Zone 3


Deeside

Causeway Geotech

Attention :

Date :

Your reference :

Our reference :

Location :


Status :

Issue :

Colm Hurley

28th February, 2017

1


CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

8 Drumahiskey Road

Bainamore

Ballymoney

Co Antrim

BT53 7QL


Four samples were received for analysis on 30th January, 2017 of which four were scheduled for analysis. Please find attached our Test Report




Phil Sommerton BSc

Project Manager

WOP 16-1239

Project Gemini

30th January, 2017

Final report

Compiled By:




For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Reference:


Contact:

JE Job No.: 17/3119

J E Sample No. 1-2 3-4 5-6 7-8


Depth 0.75 1.50 0.50 1.00

COC No / misc


Sample Date 27/01/2017 27/01/2017 27/01/2017 27/01/2017



Date of Receipt 30/01/2017 30/01/2017 30/01/2017 30/01/2017

Aluminium 8293 2604 2899 2334 <50 mg/kg TM30/PM15

Arsenic # 40.2 6.2 6.7 4.3 <0.5 mg/kg TM30/PM15

Barium # 55 17 16 15 <1 mg/kg TM30/PM15

Cadmium # 0.2 0.3 0.4 0.4 <0.1 mg/kg TM30/PM15

Chromium # 22.8 18.5 22.2 22.7 <0.5 mg/kg TM30/PM15

Copper # 10 4 8 7 <1 mg/kg TM30/PM15

Iron 23900 7366 7143 5925 <20 mg/kg TM30/PM15

Lead # 71 13 13 9 <5 mg/kg TM30/PM15

Mercury # <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM30/PM15

Molybdenum # 0.8 1.5 1.3 1.9 <0.1 mg/kg TM30/PM15

Nickel # 36.6 10.6 16.0 14.8 <0.7 mg/kg TM30/PM15

Selenium # <1 <1 <1 <1 <1 mg/kg TM30/PM15

Zinc # 641 159 72 74 <5 mg/kg TM30/PM15

PAH MS

Naphthalene # <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Acenaphthylene <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Acenaphthene # <0.05 <0.05 <0.05 <0.05 <0.05 mg/kg TM4/PM8

Fluorene # <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Phenanthrene # <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Anthracene # <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Fluoranthene # <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Pyrene # <0.03 <0.03 <0.03 <0.03 <0.03 mg/kg TM4/PM8

Benzo(a)anthracene # <0.06 <0.06 <0.06 <0.06 <0.06 mg/kg TM4/PM8

Chrysene # <0.02 <0.02 <0.02 <0.02 <0.02 mg/kg TM4/PM8

Benzo(bk)fluoranthene # <0.07 <0.07 <0.07 <0.07 <0.07 mg/kg TM4/PM8

Benzo(a)pyrene # <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Indeno(123cd)pyrene # <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Dibenzo(ah)anthracene # <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Benzo(ghi)perylene # <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

Coronene <0.04 <0.04 <0.04 <0.04 <0.04 mg/kg TM4/PM8

PAH 17 Total <0.64 <0.64 <0.64 <0.64 <0.64 mg/kg TM4/PM8

Benzo(b)fluoranthene <0.05 <0.05 <0.05 <0.05 <0.05 mg/kg TM4/PM8

Benzo(k)fluoranthene <0.02 <0.02 <0.02 <0.02 <0.02 mg/kg TM4/PM8

PAH Surrogate % Recovery 102 116 115 111 <0 % TM4/PM8

Methyl Tertiary Butyl Ether # - <2 - - <2 ug/kg TM15/PM10

Benzene # - <3 - - <3 ug/kg TM15/PM10

Toluene # - 3 - - <3 ug/kg TM15/PM10

Ethylbenzene # - <3 - - <3 ug/kg TM15/PM10

p/m-Xylene # - <5 - - <5 ug/kg TM15/PM10

o-Xylene # - <3 - - <3 ug/kg TM15/PM10

Surrogate Recovery Toluene D8 - 93 - - <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene - 63 - - <0 % TM15/PM10

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Reference:


Contact:

JE Job No.: 17/3119

J E Sample No. 1-2 3-4 5-6 7-8


Depth 0.75 1.50 0.50 1.00

COC No / misc


Sample Date 27/01/2017 27/01/2017 27/01/2017 27/01/2017



Date of Receipt 30/01/2017 30/01/2017 30/01/2017 30/01/2017

MTBE #

<5SV - <5 <5 <5 ug/kg TM31/PM12

Benzene #

<5SV - <5 <5 <5 ug/kg TM31/PM12

Toluene #

<5SV - <5 <5 <5 ug/kg TM31/PM12

Ethylbenzene #

<5SV - <5 <5 <5 ug/kg TM31/PM12

m/p-Xylene #

<5SV - <5 <5 <5 ug/kg TM31/PM12

o-Xylene #

<5SV - <5 <5 <5 ug/kg TM31/PM12

PCB 28 # - <5 - - <5 ug/kg TM17/PM8

PCB 52 # - <5 - - <5 ug/kg TM17/PM8

PCB 101 # - <5 - - <5 ug/kg TM17/PM8

PCB 118 # - <5 - - <5 ug/kg TM17/PM8

PCB 138 # - <5 - - <5 ug/kg TM17/PM8

PCB 153 # - <5 - - <5 ug/kg TM17/PM8

PCB 180 # - <5 - - <5 ug/kg TM17/PM8

Total 7 PCBs # - <35 - - <35 ug/kg TM17/PM8

Total Phenols HPLC - 0.38 - - <0.15 mg/kg TM26/PM21

Natural Moisture Content 5.2 5.5 5.6 6.5 <0.1 % PM4/PM0

Ammoniacal Nitrogen as N <0.6 3.3 <0.6 - <0.6 mg/kg TM38/PM20

Chloride # 52 50 21 - <2 mg/kg TM38/PM20

Hexavalent Chromium # <0.3 <0.3 <0.3 <0.3 <0.3 mg/kg TM38/PM20

Ortho Phosphate as PO4 <0.3 <0.3 <0.3 - <0.3 mg/kg TM38/PM20

Sulphate as SO4 (2:1 Ext) # 0.9224 0.1850 0.3027 - <0.0015 g/l TM38/PM20

Chromium III 22.8 18.5 22.2 22.7 <0.5 mg/kg NONE/NONE

LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Reference:

Location:

Contact:

JE Job No.: 17/3119

J E Sample No. 3-4

Sample ID WOP TP06/17

Depth 1.50

COC No / misc

Containers V J


Sample Type Soil

Batch Number 1

Date of Receipt 30/01/2017

SVOC MS

Phenols

2-Chlorophenol # <10 <10 ug/kg TM16/PM8

2-Methylphenol <10 <10 ug/kg TM16/PM8

2-Nitrophenol <10 <10 ug/kg TM16/PM8

2,4-Dichlorophenol # <10 <10 ug/kg TM16/PM8

2,4-Dimethylphenol <10 <10 ug/kg TM16/PM8

2,4,5-Trichlorophenol <10 <10 ug/kg TM16/PM8

2,4,6-Trichlorophenol <10 <10 ug/kg TM16/PM8

4-Chloro-3-methylphenol <10 <10 ug/kg TM16/PM8

4-Methylphenol <10 <10 ug/kg TM16/PM8

4-Nitrophenol <10 <10 ug/kg TM16/PM8

Pentachlorophenol <10 <10 ug/kg TM16/PM8

Phenol # <10 <10 ug/kg TM16/PM8

PAHs

2-Chloronaphthalene # <10 <10 ug/kg TM16/PM8

2-Methylnaphthalene # <10 <10 ug/kg TM16/PM8

Phthalates

Bis(2-ethylhexyl) phthalate <100 <100 ug/kg TM16/PM8

Butylbenzyl phthalate <100 <100 ug/kg TM16/PM8

Di-n-butyl phthalate <100 <100 ug/kg TM16/PM8

Di-n-Octyl phthalate <100 <100 ug/kg TM16/PM8

Diethyl phthalate <100 <100 ug/kg TM16/PM8

Dimethyl phthalate # <100 <100 ug/kg TM16/PM8

Other SVOCs

1,2-Dichlorobenzene <10 <10 ug/kg TM16/PM8

1,2,4-Trichlorobenzene # <10 <10 ug/kg TM16/PM8



2-Nitroaniline <10 <10 ug/kg TM16/PM8

2,4-Dinitrotoluene <10 <10 ug/kg TM16/PM8

2,6-Dinitrotoluene <10 <10 ug/kg TM16/PM8


4-Bromophenylphenylether # <10 <10 ug/kg TM16/PM8

4-Chloroaniline <10 <10 ug/kg TM16/PM8

4-Chlorophenylphenylether <10 <10 ug/kg TM16/PM8


Azobenzene <10 <10 ug/kg TM16/PM8

Bis(2-chloroethoxy)methane <10 <10 ug/kg TM16/PM8

Bis(2-chloroethyl)ether <10 <10 ug/kg TM16/PM8

Carbazole <10 <10 ug/kg TM16/PM8

Dibenzofuran # <10 <10 ug/kg TM16/PM8

Hexachlorobenzene <10 <10 ug/kg TM16/PM8

Hexachlorobutadiene # <10 <10 ug/kg TM16/PM8

Hexachlorocyclopentadiene <10 <10 ug/kg TM16/PM8

Hexachloroethane <10 <10 ug/kg TM16/PM8

Isophorone # <10 <10 ug/kg TM16/PM8

N-nitrosodi-n-propylamine # <10 <10 ug/kg TM16/PM8

Nitrobenzene # <10 <10 ug/kg TM16/PM8

Surrogate Recovery 2-Fluorobiphenyl 73 <0 % TM16/PM8

Surrogate Recovery p-Terphenyl-d14 97 <0 % TM16/PM8

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Reference:

Location:

Contact:

JE Job No.: 17/3119

J E Sample No. 3-4


Depth 1.50

COC No / misc

Containers V J


Sample Type Soil

Batch Number 1


VOC MS

Dichlorodifluoromethane <2 <2 ug/kg TM15/PM10

Methyl Tertiary Butyl Ether # <2 <2 ug/kg TM15/PM10

Chloromethane # <3 <3 ug/kg TM15/PM10

Vinyl Chloride <2 <2 ug/kg TM15_A/PM10

Bromomethane <1 <1 ug/kg TM15/PM10

Chloroethane # <2 <2 ug/kg TM15/PM10

Trichlorofluoromethane # <2 <2 ug/kg TM15/PM10

1,1-Dichloroethene (1,1 DCE) # <6 <6 ug/kg TM15/PM10

Dichloromethane (DCM) # 45 <30 ug/kg TM15/PM10

trans-1-2-Dichloroethene # <3 <3 ug/kg TM15/PM10

1,1-Dichloroethane # <3 <3 ug/kg TM15/PM10

cis-1-2-Dichloroethene # <3 <3 ug/kg TM15/PM10

2,2-Dichloropropane <4 <4 ug/kg TM15/PM10

Bromochloromethane # <3 <3 ug/kg TM15/PM10

Chloroform # <3 <3 ug/kg TM15/PM10

1,1,1-Trichloroethane # <3 <3 ug/kg TM15/PM10

1,1-Dichloropropene # <3 <3 ug/kg TM15/PM10

Carbon tetrachloride # <4 <4 ug/kg TM15/PM10

1,2-Dichloroethane # <4 <4 ug/kg TM15/PM10

Benzene # <3 <3 ug/kg TM15/PM10

Trichloroethene (TCE) # <3 <3 ug/kg TM15/PM10

1,2-Dichloropropane # <6 <6 ug/kg TM15/PM10

Dibromomethane # <3 <3 ug/kg TM15/PM10

Bromodichloromethane # <3 <3 ug/kg TM15/PM10

cis-1-3-Dichloropropene <4 <4 ug/kg TM15/PM10

Toluene # 3 <3 ug/kg TM15/PM10

trans-1-3-Dichloropropene <3 <3 ug/kg TM15/PM10

1,1,2-Trichloroethane # <3 <3 ug/kg TM15/PM10

Tetrachloroethene (PCE) # <3 <3 ug/kg TM15/PM10

1,3-Dichloropropane # <3 <3 ug/kg TM15/PM10

Dibromochloromethane # <3 <3 ug/kg TM15/PM10

1,2-Dibromoethane # <3 <3 ug/kg TM15/PM10

Chlorobenzene # <3 <3 ug/kg TM15/PM10

1,1,1,2-Tetrachloroethane <3 <3 ug/kg TM15/PM10

Ethylbenzene # <3 <3 ug/kg TM15/PM10

p/m-Xylene # <5 <5 ug/kg TM15/PM10

o-Xylene # <3 <3 ug/kg TM15/PM10

Styrene <3 <3 ug/kg TM15_A/PM10

Bromoform <3 <3 ug/kg TM15/PM10

Isopropylbenzene # <3 <3 ug/kg TM15/PM10

1,1,2,2-Tetrachloroethane # <3 <3 ug/kg TM15/PM10

Bromobenzene <2 <2 ug/kg TM15/PM10

1,2,3-Trichloropropane # <4 <4 ug/kg TM15/PM10

Propylbenzene # <4 <4 ug/kg TM15/PM10

2-Chlorotoluene <3 <3 ug/kg TM15/PM10

1,3,5-Trimethylbenzene # <3 <3 ug/kg TM15/PM10

4-Chlorotoluene <3 <3 ug/kg TM15/PM10

tert-Butylbenzene # <5 <5 ug/kg TM15/PM10

1,2,4-Trimethylbenzene # <6 <6 ug/kg TM15/PM10

sec-Butylbenzene # <4 <4 ug/kg TM15/PM10

4-Isopropyltoluene # <4 <4 ug/kg TM15/PM10

1,3-Dichlorobenzene # <4 <4 ug/kg TM15/PM10


n-Butylbenzene # <4 <4 ug/kg TM15/PM10


1,2-Dibromo-3-chloropropane # <4 <4 ug/kg TM15/PM10


Hexachlorobutadiene <4 <4 ug/kg TM15/PM10

Naphthalene <27 <27 ug/kg TM15/PM10


Surrogate Recovery Toluene D8 93 <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 63 <0 % TM15/PM10

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

Client Name:

Reference:

Location:

Contact:

Note:

J E

Job

No.

Batch Depth

J E

Sample

No.

Date Of


17/3119 1 0.75 2 07/02/2017 General Description (Bulk Analysis) Soil/Stones








17/3119 1 0.50 6 07/02/2017 General Description (Bulk Analysis) Soil/Stones








WOP TP07/17

Ryan Butterworth


Sample ID

WOP TP06/17





sampling.



Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


J E

Job

No.


No.Analysis Reason




WOP 16-1239

Project Gemini

Colm HurleyContact:

Sample ID


Reference:

Location:



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

BLANKS

NOTE






















accredited.

















17/3119

WATERS


blanks.





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

JE Job No.:

#

SA

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

Dilution required.


Matrix Effect

Blank Sample

Client Sample

Trip Blank Sample

AQC Sample




17/3119



Not applicable






MCERTS accredited.


No Fibres Detected








For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis






by GC-MS. PM8




by GC-MS. PM8









TM5/TM36







PM12/PM16



Trace SPE.

AR Yes











For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis















TM21


























For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

























AD Yes







Yes AD Yes







AR Yes







Yes AR Yes

TM60







For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis























For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis







For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Zone 3


Deeside

Causeway Geotech

Attention :

Date :

Your reference :

Our reference :

Location :


Status :

Issue :

Colm Hurley

28th February, 2017

1


CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

8 Drumahiskey Road

Bainamore

Ballymoney

Co Antrim

BT53 7QL


One sample was received for analysis on 30th January, 2017 of which one were scheduled for analysis. Please find attached our Test Report






Phil Sommerton BSc

Project Manager

WOP 16-1239

Project Gemini

30th January, 2017

Final report

Compiled By:




For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Reference:


Contact:

JE Job No.: 17/3119

J E Sample No. 9-10


Depth 0.50-1.50

COC No / misc

Containers V J


Sample Type Soil

Batch Number 1


Antimony <1 <1 mg/kg TM30/PM15

Arsenic # 5.9 <0.5 mg/kg TM30/PM15

Barium # 15 <1 mg/kg TM30/PM15

Cadmium # 0.3 <0.1 mg/kg TM30/PM15

Chromium # 88.5 <0.5 mg/kg TM30/PM15

Copper # 5 <1 mg/kg TM30/PM15

Lead # 11 <5 mg/kg TM30/PM15

Mercury # <0.1 <0.1 mg/kg TM30/PM15

Molybdenum # 6.1 <0.1 mg/kg TM30/PM15

Nickel # 13.0 <0.7 mg/kg TM30/PM15

Selenium # <1 <1 mg/kg TM30/PM15

Zinc # 87 <5 mg/kg TM30/PM15

PAH MS

Naphthalene # <0.04 <0.04 mg/kg TM4/PM8

Acenaphthylene <0.03 <0.03 mg/kg TM4/PM8

Acenaphthene # <0.05 <0.05 mg/kg TM4/PM8

Fluorene # <0.04 <0.04 mg/kg TM4/PM8

Phenanthrene # <0.03 <0.03 mg/kg TM4/PM8

Anthracene # <0.04 <0.04 mg/kg TM4/PM8

Fluoranthene # <0.03 <0.03 mg/kg TM4/PM8

Pyrene # <0.03 <0.03 mg/kg TM4/PM8

Benzo(a)anthracene # <0.06 <0.06 mg/kg TM4/PM8

Chrysene # <0.02 <0.02 mg/kg TM4/PM8

Benzo(bk)fluoranthene # <0.07 <0.07 mg/kg TM4/PM8

Benzo(a)pyrene # <0.04 <0.04 mg/kg TM4/PM8

Indeno(123cd)pyrene # <0.04 <0.04 mg/kg TM4/PM8

Dibenzo(ah)anthracene # <0.04 <0.04 mg/kg TM4/PM8

Benzo(ghi)perylene # <0.04 <0.04 mg/kg TM4/PM8

Coronene <0.04 <0.04 mg/kg TM4/PM8

PAH 6 Total # <0.22 <0.22 mg/kg TM4/PM8

PAH 17 Total <0.64 <0.64 mg/kg TM4/PM8

Benzo(b)fluoranthene <0.05 <0.05 mg/kg TM4/PM8

Benzo(k)fluoranthene <0.02 <0.02 mg/kg TM4/PM8

Benzo(j)fluoranthene <1 <1 mg/kg TM4/PM8

PAH Surrogate % Recovery 115 <0 % TM4/PM8

Mineral Oil (C10-C40) <30 <30 mg/kg TM5/PM16

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:40


Reference:


Contact:

JE Job No.: 17/3119

J E Sample No. 9-10


Depth 0.50-1.50

COC No / misc

Containers V J


Sample Type Soil

Batch Number 1


TPH CWG

Aliphatics

>C5-C6 #

<0.1SV <0.1 mg/kg TM36/PM12

>C6-C8 #

<0.1SV <0.1 mg/kg TM36/PM12

>C8-C10 <0.1SV <0.1 mg/kg TM36/PM12

>C10-C12 # <0.2 <0.2 mg/kg TM5/PM16

>C12-C16 # <4 <4 mg/kg TM5/PM16

>C16-C21 # <7 <7 mg/kg TM5/PM16

>C21-C35 # <7 <7 mg/kg TM5/PM16

>C35-C40 <7 <7 mg/kg TM5/PM16

Total aliphatics C5-40 <26 <26 mg/kg TM5/TM36/PM12/PM16

>C6-C10 <0.1SV <0.1 mg/kg TM36/PM12

>C10-C25 <10 <10 mg/kg TM5/PM16

>C25-C35 <10 <10 mg/kg TM5/PM16

Aromatics

>C5-EC7 #

<0.1SV <0.1 mg/kg TM36/PM12

>EC7-EC8 #

<0.1SV <0.1 mg/kg TM36/PM12

>EC8-EC10 #

<0.1SV <0.1 mg/kg TM36/PM12

>EC10-EC12 # <0.2 <0.2 mg/kg TM5/PM16

>EC12-EC16 # <4 <4 mg/kg TM5/PM16

>EC16-EC21 # <7 <7 mg/kg TM5/PM16

>EC21-EC35 # <7 <7 mg/kg TM5/PM16

>EC35-EC40 <7 <7 mg/kg TM5/PM16

Total aromatics C5-40 <26 <26 mg/kg TM5/TM36/PM12/PM16

Total aliphatics and aromatics(C5-40) <52 <52 mg/kg TM5/TM36/PM12/PM16

>EC6-EC10 #

<0.1SV <0.1 mg/kg TM36/PM12

>EC10-EC25 <10 <10 mg/kg TM5/PM16

>EC25-EC35 <10 <10 mg/kg TM5/PM16

MTBE #


Benzene #


Toluene #


Ethylbenzene #


m/p-Xylene #


o-Xylene #


PCB 28 # <5 <5 ug/kg TM17/PM8

PCB 52 # <5 <5 ug/kg TM17/PM8

PCB 101 # <5 <5 ug/kg TM17/PM8

PCB 118 # <5 <5 ug/kg TM17/PM8

PCB 138 # <5 <5 ug/kg TM17/PM8

PCB 153 # <5 <5 ug/kg TM17/PM8

PCB 180 # <5 <5 ug/kg TM17/PM8

Total 7 PCBs # <35 <35 ug/kg TM17/PM8

LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


Reference:


Contact:

JE Job No.: 17/3119

J E Sample No. 9-10


Depth 0.50-1.50

COC No / misc

Containers V J


Sample Type Soil

Batch Number 1


Natural Moisture Content 5.9 <0.1 % PM4/PM0

Moisture Content (% Wet Weight) 5.5 <0.1 % PM4/PM0

Hexavalent Chromium # <0.3 <0.3 mg/kg TM38/PM20

Chromium III 88.5 <0.5 mg/kg NONE/NONE

Total Organic Carbon # 0.44 <0.02 % TM21/PM24

pH # 7.80 <0.01 pH units TM73/PM11

Mass of raw test portion 0.1 kg NONE/PM17

Mass of dried test portion 0.09 kg NONE/PM17

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


Reference:


Contact:

JE Job No.: 17/3119

J E Sample No. 9-10


Depth 0.50-1.50

COC No / misc

Containers V J


Sample Type Soil

Batch Number 1


Dissolved Antimony # <0.002 <0.002 mg/l TM30/PM17

Dissolved Antimony (A10) # <0.02 <0.02 mg/kg TM30/PM17

Dissolved Arsenic # <0.0025 <0.0025 mg/l TM30/PM17

Dissolved Arsenic (A10) # <0.025 <0.025 mg/kg TM30/PM17

Dissolved Barium # 0.013 <0.003 mg/l TM30/PM17

Dissolved Barium (A10) # 0.13 <0.03 mg/kg TM30/PM17

Dissolved Cadmium # <0.0005 <0.0005 mg/l TM30/PM17

Dissolved Cadmium (A10) # <0.005 <0.005 mg/kg TM30/PM17

Dissolved Chromium # <0.0015 <0.0015 mg/l TM30/PM17

Dissolved Chromium (A10) # <0.015 <0.015 mg/kg TM30/PM17

Dissolved Copper # <0.007 <0.007 mg/l TM30/PM17

Dissolved Copper (A10) # <0.07 <0.07 mg/kg TM30/PM17

Dissolved Lead # <0.005 <0.005 mg/l TM30/PM17

Dissolved Lead (A10) # <0.05 <0.05 mg/kg TM30/PM17

Dissolved Molybdenum # 0.004 <0.002 mg/l TM30/PM17

Dissolved Molybdenum (A10) # 0.04 <0.02 mg/kg TM30/PM17

Dissolved Nickel # <0.002 <0.002 mg/l TM30/PM17

Dissolved Nickel (A10) # <0.02 <0.02 mg/kg TM30/PM17

Dissolved Selenium # <0.003 <0.003 mg/l TM30/PM17

Dissolved Selenium (A10) # <0.03 <0.03 mg/kg TM30/PM17

Dissolved Zinc # 0.004 <0.003 mg/l TM30/PM17

Dissolved Zinc (A10) # 0.04 <0.03 mg/kg TM30/PM17

Mercury Dissolved by CVAF # <0.00001 <0.00001 mg/l TM61/PM38

Mercury Dissolved by CVAF # <0.0001 <0.0001 mg/kg TM61/PM38

Phenol <0.01 <0.01 mg/l TM26/PM0

Phenol <0.1 <0.1 mg/kg TM26/PM0

Fluoride <0.3 <0.3 mg/l TM173/PM0

Fluoride <3 <3 mg/kg TM173/PM0

Sulphate # 88.12 <0.05 mg/l TM38/PM0

Sulphate # 881.2 <0.5 mg/kg TM38/PM0

Chloride # 1.0 <0.3 mg/l TM38/PM0

Chloride # 10 <3 mg/kg TM38/PM0

Leachant Volume 0.89 l NONE/PM17

Eluate Volume 0.82 l NONE/PM17

Dissolved Organic Carbon <2 <2 mg/l TM60/PM0

Dissolved Organic Carbon <20 <20 mg/kg TM60/PM0

pH 8.51 <0.01 pH units TM73/PM0

Total Dissolved Solids # 177 <35 mg/l TM20/PM0

Total Dissolved Solids # 1770 <350 mg/kg TM20/PM0

Project Gemini

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

WOP 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41




JEFL Job No

Sample No

Client Sample No

Depth/Other

Sample Date

Batch No




Sum of 7 PCBs (mg/kg) <0.035 1 - -


PAH Sum of 6 (mg/kg) <0.22 - - -

PAH Sum of 17 (mg/kg) <0.64 100 - -

10:1

concn

leached

A10

mg/kg

Arsenic <0.025 0.5 2 25

Barium 0.13 20 100 300

Cadmium <0.005 0.04 1 5

Chromium <0.015 0.5 10 70

Copper <0.07 2 50 100

Mercury <0.0001 0.01 0.2 2


Nickel <0.02 0.4 10 40

Lead <0.05 0.5 10 50

Antimony <0.02 0.06 0.7 5

Selenium <0.03 0.1 0.5 7

Zinc 0.04 4 50 200

Chloride 10 800 15000 25000

Fluoride <3 10 150 500

Sulphate as SO4 881.2 1000 20000 50000


Phenol <0.1 1 - -

Dissolved Organic Carbon <20 500 800 1000

27/01/2017

1

Eluate Analysis


leaching test using

BS EN 12457-2 at L/S 10 l/kg

mg/kg



Criteria Limits 10

WOP TP06/17

InertStable


0.50-1.50



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

EPH Interpretation Report

Matrix : Solid

J E

Job

No.


No.EPH Interpretation


Contact: Colm Hurley

Sample ID

WOP TP06/17


Reference: WOP 16-1239

Location: Project Gemini



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

Client Name:

Reference:

Location:

Contact:

Note:

J E

Job

No.

Batch Depth

J E

Sample

No.

Date Of


17/3119 1 0.50-1.50 10 07/02/2017 General Description (Bulk Analysis) Soil/Stones








Ryan Butterworth


Sample ID

WOP TP06/17





sampling.



Causeway Geotech

WOP 16-1239

Project Gemini

Colm Hurley


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


J E

Job

No.


No.Analysis Reason




WOP 16-1239

Project Gemini

Colm HurleyContact:

Sample ID


Reference:

Location:



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

BLANKS

NOTE






















accredited.

















17/3119

WATERS


blanks.





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

JE Job No.:

#

SA

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

Dilution required.


Matrix Effect

Blank Sample

Client Sample

Trip Blank Sample

AQC Sample




17/3119



Not applicable






MCERTS accredited.


No Fibres Detected








For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis






by GC-MS. PM8




by GC-MS. PM8









TM5/TM36







PM12/PM16



Trace SPE.

AR Yes











For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis















TM21


























For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

























AD Yes







Yes AD Yes







AR Yes







Yes AR Yes

TM60







For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis























For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

JE Job No: 17/3119


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis







For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41

Leachate tests

10l/kg; 4mmI.S. EN 12457-2:2002 Specified particle size; water added to L/S ratio; capped; agitated for 24 ± 0.5 hours; eluate settled and

filtered over 0.45 μm membrane filter.

Eluate analysis

As I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Ba I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Cd I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Cr total I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Cu I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Hg I.S. EN 13370 rec. EN 1483 (CVAAS)

Mo I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Ni I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Pb I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Sb I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Se I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Zn I.S. EN 12506 : EN ISO 11885 (ICP-OES)

Chloride I.S. EN 12506 rec. EN ISO 10304-part 1 (liquid chromatography of ions)

Fluoride I.S. EN 12506 rec. EN ISO 10304-part 1 (liquid chromatography of ions)

Sulphate I.S. EN 12506 rec. EN ISO 10304-part 1 (liquid chromatography of ions)

Phenol index I.S. EN 13370 rec. ISO 6439 (4-Aminoantipyrine spectrometic methods after distillation)* ( BY HPLC - Jones Env)

DOC I.S. EN 1484

TDS I.S. EN 15216

Compositional analysis

TOC I.S. EN 13137 Method B: carbonates removed with acid; TOC by combustion.

BTEX GC-FID

PCB7** I.S. EN 15308 analysis by GC-ECD.

Mineral oil I.S. EN 14039 C10 to C40 analysis by GC-FID.

PAH17*** I.S. EN 15527 PAH17 analysis by GC-MS

Metals I.S. EN 13657 - Aqua regia digestion: EN ISO 11885 ( ICP-OES)

Other

Dry matter

I.S. EN 14346 sample is dried to a constant mass in an oven at 105 ± 3 °C; Method B Water content by direct Karl-Fischer-

titration and either volumetric or coulometric detection.

LOI I.S. EN 15169 Difference in mass after heating in a furnace up to 550 ± 25 °C.

ANC CEN/TS 15364 Determined by amouns of acid or base needed to cover the pH range

Notes:

*If not suitable due to LOD, precision, etc., any other suitable method can be used, e.g. AFS, ICP-MS

**PCB-28, PCB-52, PCB-101, PCB-118, PCB-138, PCB-153 and PCB-180

Appendix - Methods used for WAC (2003/33/EC)

***Naphthalene, Acenaphthylene, Acenaphthene, Anthracene, Benzo(a)anthracene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(g,h,i)perylene,

Benzo(a)pyrene, Chrysene, Coronene, Dibenzo(a,h)anthracene, Fluorene, Fluoranthene, Indeno(1,2,3-c,d)pyrene, Phenanthrene and Pyrene.


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


Zone 3


Deeside

Causeway Geotech

Attention :

Date :

Your reference :

Our reference :

Location :


Status :

Issue :

Colm Hurley

13th February, 2017

1


CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

8 Drumahiskey Road

Bainamore

Ballymoney

Co Antrim

BT53 7QL


Eighteen samples were received for analysis on 1st February, 2017 of which fourteen were scheduled for analysis. Please find attached our Test

Report which should be read with notes at the end of the report and should include all sections if reproduced. Interpretations and opinions are

outside the scope of any accreditation, and all results relate only to samples supplied.


Phil Sommerton BSc

Project Manager

Gemini 16-1239

WOP-ADF

1st February, 2017

Final report

Compiled By:




For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


Reference:


Contact:

JE Job No.: 17/3272

J E Sample No. 1-2 3-4 5-6 7-8 11-12 15-16 17-18 21-22 23-24 25-26

Sample IDWOP-ADF

TP02/17

WOP-ADF

TP02/17

WOP-ADF

TP03/17

WOP-ADF

TP03/17

WOP-ADF

TP04/17

WOP-ADF

TP05/17

WOP-ADF

TP06/17

WOP-ADF

TP07/17

WOP-ADF

TP08/17

WOP-ADF

TP08/17

Depth 1.50 2.50 0.50 1.50 2.50 2.00 1.00 1.50 0.50 2.50

COC No / misc


Sample Date 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017


Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017

Aluminium 212 7575 23690 9008 6804 4400 974 1352 - 1559 <50 mg/kg TM30/PM15

Arsenic # 0.5 7.5 5.2 2.0 11.1 2.9 2.5 1.1 - 1.4 <0.5 mg/kg TM30/PM15

Barium # 34 47 120 28 88 19 29 8 - 9 <1 mg/kg TM30/PM15

Cadmium # <0.1 1.0 0.7 0.2 1.0 0.8 0.2 0.7 - 0.6 <0.1 mg/kg TM30/PM15

Chromium # 19.0 27.7 58.9 27.5 30.9 29.6 33.9 17.1 - 15.2 <0.5 mg/kg TM30/PM15

Copper # 2 15 34 11 16 11 5 5 - 6 <1 mg/kg TM30/PM15

Iron 4812 10640 16960 13320 14140 6663 6474 3045 - 5475 <20 mg/kg TM30/PM15

Lead # <5 13 31 12 13 9 <5 5 - <5 <5 mg/kg TM30/PM15

Mercury # <0.1 <0.1 <0.1 <0.1 0.2 <0.1 <0.1 <0.1 - <0.1 <0.1 mg/kg TM30/PM15

Molybdenum # 2.1 1.6 1.0 0.6 2.4 2.2 3.1 0.6 - 0.6 <0.1 mg/kg TM30/PM15

Nickel # 3.8 37.7 75.0 31.1 34.1 24.5 10.3 9.9 - 12.5 <0.7 mg/kg TM30/PM15

Selenium # 2 <1 1 <1 2 <1 2 <1 - <1 <1 mg/kg TM30/PM15

Zinc # <5 69 121 62 64 36 9 23 - 26 <5 mg/kg TM30/PM15

PAH MS

Naphthalene # - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

Acenaphthylene - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 mg/kg TM4/PM8

Acenaphthene # - <0.05 <0.05 <0.05 - - <0.05 <0.05 - - <0.05 mg/kg TM4/PM8

Fluorene # - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

Phenanthrene # - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 mg/kg TM4/PM8

Anthracene # - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

Fluoranthene # - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 mg/kg TM4/PM8

Pyrene # - <0.03 <0.03 <0.03 - - <0.03 <0.03 - - <0.03 mg/kg TM4/PM8

Benzo(a)anthracene # - <0.06 <0.06 <0.06 - - <0.06 <0.06 - - <0.06 mg/kg TM4/PM8

Chrysene # - <0.02 <0.02 <0.02 - - <0.02 <0.02 - - <0.02 mg/kg TM4/PM8

Benzo(bk)fluoranthene # - <0.07 <0.07 <0.07 - - <0.07 <0.07 - - <0.07 mg/kg TM4/PM8

Benzo(a)pyrene # - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

Indeno(123cd)pyrene # - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

Dibenzo(ah)anthracene # - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

Benzo(ghi)perylene # - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

Coronene - <0.04 <0.04 <0.04 - - <0.04 <0.04 - - <0.04 mg/kg TM4/PM8

PAH 17 Total - <0.64 <0.64 <0.64 - - <0.64 <0.64 - - <0.64 mg/kg TM4/PM8

Benzo(b)fluoranthene - <0.05 <0.05 <0.05 - - <0.05 <0.05 - - <0.05 mg/kg TM4/PM8

Benzo(k)fluoranthene - <0.02 <0.02 <0.02 - - <0.02 <0.02 - - <0.02 mg/kg TM4/PM8

PAH Surrogate % Recovery - 117 121 112 - - 118 118 - - <0 % TM4/PM8

Methyl Tertiary Butyl Ether # - - <2 <2 - - - <2 - - <2 ug/kg TM15/PM10

Benzene # - - <3 <3 - - - <3 - - <3 ug/kg TM15/PM10

Toluene # - - <3 <3 - - - <3 - - <3 ug/kg TM15/PM10

Ethylbenzene # - - <3 <3 - - - <3 - - <3 ug/kg TM15/PM10

p/m-Xylene # - - <5 <5 - - - <5 - - <5 ug/kg TM15/PM10

o-Xylene # - - <3 <3 - - - <3 - - <3 ug/kg TM15/PM10

Surrogate Recovery Toluene D8 - - 102 99 - - - 102 - - <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene - - 105 90 - - - 114 - - <0 % TM15/PM10

WOP-ADF

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


Reference:


Contact:

JE Job No.: 17/3272

J E Sample No. 1-2 3-4 5-6 7-8 11-12 15-16 17-18 21-22 23-24 25-26

Sample IDWOP-ADF

TP02/17

WOP-ADF

TP02/17

WOP-ADF

TP03/17

WOP-ADF

TP03/17

WOP-ADF

TP04/17

WOP-ADF

TP05/17

WOP-ADF

TP06/17

WOP-ADF

TP07/17

WOP-ADF

TP08/17

WOP-ADF

TP08/17

Depth 1.50 2.50 0.50 1.50 2.50 2.00 1.00 1.50 0.50 2.50

COC No / misc


Sample Date 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017


Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017

TPH CWG

Aliphatics

>C5-C6 # - - - <0.1 - - - <0.1 - - <0.1 mg/kg TM36/PM12

>C6-C8 # - - - <0.1 - - - <0.1 - - <0.1 mg/kg TM36/PM12

>C8-C10 - - - <0.1 - - - <0.1 - - <0.1 mg/kg TM36/PM12

>C10-C12 # - - - <0.2 - - - <0.2 - - <0.2 mg/kg TM5/PM16

>C12-C16 # - - - <4 - - - <4 - - <4 mg/kg TM5/PM16

>C16-C21 # - - - <7 - - - <7 - - <7 mg/kg TM5/PM16

>C21-C35 # - - - <7 - - - <7 - - <7 mg/kg TM5/PM16

Total aliphatics C5-35 - - - <19 - - - <19 - - <19 mg/kg TM5/TM36/PM12/PM16

Aromatics

>C5-EC7 # - - - <0.1 - - - <0.1 - - <0.1 mg/kg TM36/PM12

>EC7-EC8 # - - - <0.1 - - - <0.1 - - <0.1 mg/kg TM36/PM12

>EC8-EC10 # - - - <0.1 - - - <0.1 - - <0.1 mg/kg TM36/PM12

>EC10-EC12 # - - - <0.2 - - - <0.2 - - <0.2 mg/kg TM5/PM16

>EC12-EC16 # - - - <4 - - - <4 - - <4 mg/kg TM5/PM16

>EC16-EC21 # - - - <7 - - - <7 - - <7 mg/kg TM5/PM16

>EC21-EC35 # - - - <7 - - - <7 - - <7 mg/kg TM5/PM16

Total aromatics C5-35 # - - - <19 - - - <19 - - <19 mg/kg TM5/TM36/PM12/PM16

Total aliphatics and aromatics(C5-35) - - - <38 - - - <38 - - <38 mg/kg TM5/TM36/PM12/PM16

Natural Moisture Content 472.4 28.1 38.7 14.7 50.3 14.0 780.0 12.5 878.3 9.3 <0.1 % PM4/PM0

Ammoniacal Nitrogen as N 17.2 - - <0.6 - - - <0.6 28.4 - <0.6 mg/kg TM38/PM20

Chloride # 148 - - 24 - - - 22 121 - <2 mg/kg TM38/PM20

Hexavalent Chromium # <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 - <0.3 <0.3 mg/kg TM38/PM20

Ortho Phosphate as PO4 <0.3 - - <0.3 - - - <0.3 5.6 - <0.3 mg/kg TM38/PM20

Sulphate as SO4 (2:1 Ext) # 0.0820 - - 0.0243 - - - 0.0038 0.0115 - <0.0015 g/l TM38/PM20

Chromium III 19.0 27.7 58.9 27.5 30.9 29.6 33.9 17.1 - 15.2 <0.5 mg/kg NONE/NONE

Organic Matter - - - 0.5 - - - 0.2 - - <0.2 % TM21/PM24

LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239

WOP-ADF

Colm Hurley





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


Reference:


Contact:

JE Job No.: 17/3272

J E Sample No. 27-28 31-32 33-34 35-36

Sample IDWOP-ADF

TP09/17

WOP-ADF

TP10/17

WOP-ADF

TP01/17

WOP-ADF

TP01/17

Depth 1.00 1.00 1.50 3.00

COC No / misc


Sample Date 30/01/2017 30/01/2017 30/01/2017 30/01/2017



Date of Receipt 01/02/2017 01/02/2017 01/02/2017 01/02/2017

Aluminium 1393 7952 511 4662 <50 mg/kg TM30/PM15

Arsenic # 1.0 3.3 0.7 5.9 <0.5 mg/kg TM30/PM15

Barium # 9 31 9 25 <1 mg/kg TM30/PM15

Cadmium # 0.9 0.5 <0.1 0.9 <0.1 mg/kg TM30/PM15

Chromium # 17.4 48.6 16.5 32.2 <0.5 mg/kg TM30/PM15

Copper # 5 15 3 11 <1 mg/kg TM30/PM15

Iron 2574 8603 1168 8860 <20 mg/kg TM30/PM15

Lead # 7 11 <5 10 <5 mg/kg TM30/PM15

Mercury # <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM30/PM15

Molybdenum # 0.8 3.1 1.3 2.2 <0.1 mg/kg TM30/PM15

Nickel # 9.2 37.9 2.9 28.7 <0.7 mg/kg TM30/PM15

Selenium # <1 1 <1 <1 <1 mg/kg TM30/PM15

Zinc # 18 58 <5 48 <5 mg/kg TM30/PM15

PAH MS

Naphthalene # <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

Acenaphthylene <0.03 - <0.03 <0.03 <0.03 mg/kg TM4/PM8

Acenaphthene # <0.05 - <0.05 <0.05 <0.05 mg/kg TM4/PM8

Fluorene # <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

Phenanthrene # <0.03 - <0.03 <0.03 <0.03 mg/kg TM4/PM8

Anthracene # <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

Fluoranthene # <0.03 - <0.03 <0.03 <0.03 mg/kg TM4/PM8

Pyrene # <0.03 - <0.03 <0.03 <0.03 mg/kg TM4/PM8

Benzo(a)anthracene # <0.06 - <0.06 <0.06 <0.06 mg/kg TM4/PM8

Chrysene # <0.02 - <0.02 <0.02 <0.02 mg/kg TM4/PM8

Benzo(bk)fluoranthene # <0.07 - <0.07 <0.07 <0.07 mg/kg TM4/PM8

Benzo(a)pyrene # <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

Indeno(123cd)pyrene # <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

Dibenzo(ah)anthracene # <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

Benzo(ghi)perylene # <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

Coronene <0.04 - <0.04 <0.04 <0.04 mg/kg TM4/PM8

PAH 17 Total <0.64 - <0.64 <0.64 <0.64 mg/kg TM4/PM8

Benzo(b)fluoranthene <0.05 - <0.05 <0.05 <0.05 mg/kg TM4/PM8

Benzo(k)fluoranthene <0.02 - <0.02 <0.02 <0.02 mg/kg TM4/PM8

PAH Surrogate % Recovery 108 - 97 114 <0 % TM4/PM8

Methyl Tertiary Butyl Ether # <2 - <2 <2 <2 ug/kg TM15/PM10

Benzene # <3 - <3 <3 <3 ug/kg TM15/PM10

Toluene # <3 - <3 <3 <3 ug/kg TM15/PM10

Ethylbenzene # <3 - <3 <3 <3 ug/kg TM15/PM10

p/m-Xylene # <5 - <5 <5 <5 ug/kg TM15/PM10

o-Xylene # <3 - <3 <3 <3 ug/kg TM15/PM10

Surrogate Recovery Toluene D8 101 - 83 101 <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 114 - 71 88 <0 % TM15/PM10

WOP-ADF

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:41


Reference:


Contact:

JE Job No.: 17/3272

J E Sample No. 27-28 31-32 33-34 35-36

Sample IDWOP-ADF

TP09/17

WOP-ADF

TP10/17

WOP-ADF

TP01/17

WOP-ADF

TP01/17

Depth 1.00 1.00 1.50 3.00

COC No / misc


Sample Date 30/01/2017 30/01/2017 30/01/2017 30/01/2017



Date of Receipt 01/02/2017 01/02/2017 01/02/2017 01/02/2017

TPH CWG

Aliphatics

>C5-C6 # <0.1 - - <0.1 <0.1 mg/kg TM36/PM12

>C6-C8 # <0.1 - - <0.1 <0.1 mg/kg TM36/PM12

>C8-C10 <0.1 - - <0.1 <0.1 mg/kg TM36/PM12

>C10-C12 # <0.2 - - <0.2 <0.2 mg/kg TM5/PM16

>C12-C16 # <4 - - <4 <4 mg/kg TM5/PM16

>C16-C21 # <7 - - <7 <7 mg/kg TM5/PM16

>C21-C35 # <7 - - <7 <7 mg/kg TM5/PM16

Total aliphatics C5-35 <19 - - <19 <19 mg/kg TM5/TM36/PM12/PM16

Aromatics

>C5-EC7 # <0.1 - - <0.1 <0.1 mg/kg TM36/PM12

>EC7-EC8 # <0.1 - - <0.1 <0.1 mg/kg TM36/PM12

>EC8-EC10 # <0.1 - - <0.1 <0.1 mg/kg TM36/PM12

>EC10-EC12 # <0.2 - - <0.2 <0.2 mg/kg TM5/PM16

>EC12-EC16 # <4 - - <4 <4 mg/kg TM5/PM16

>EC16-EC21 # <7 - - <7 <7 mg/kg TM5/PM16

>EC21-EC35 # <7 - - <7 <7 mg/kg TM5/PM16

Total aromatics C5-35 # <19 - - <19 <19 mg/kg TM5/TM36/PM12/PM16

Total aliphatics and aromatics(C5-35) <38 - - <38 <38 mg/kg TM5/TM36/PM12/PM16

Natural Moisture Content 11.5 17.7 670.0 15.6 <0.1 % PM4/PM0

Ammoniacal Nitrogen as N - - - 4.9 <0.6 mg/kg TM38/PM20

Chloride # - - - 29 <2 mg/kg TM38/PM20

Hexavalent Chromium # <0.3 <0.3 <0.3 <0.3 <0.3 mg/kg TM38/PM20

Ortho Phosphate as PO4 - - - <0.3 <0.3 mg/kg TM38/PM20

Sulphate as SO4 (2:1 Ext) # - - - 0.0111 <0.0015 g/l TM38/PM20

Chromium III 17.4 48.6 16.5 32.2 <0.5 mg/kg NONE/NONE

Organic Matter - - - 1.0 <0.2 % TM21/PM24

LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239

WOP-ADF

Colm Hurley





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


Reference:


Contact:

JE Job No.: 17/3272

J E Sample No. 1-2 3-4 5-6 7-8 11-12 15-16 17-18 21-22 23-24 25-26

Sample IDWOP-ADF

TP02/17

WOP-ADF

TP02/17

WOP-ADF

TP03/17

WOP-ADF

TP03/17

WOP-ADF

TP04/17

WOP-ADF

TP05/17

WOP-ADF

TP06/17

WOP-ADF

TP07/17

WOP-ADF

TP08/17

WOP-ADF

TP08/17

Depth 1.50 2.50 0.50 1.50 2.50 2.00 1.00 1.50 0.50 2.50

COC No / misc


Sample Date 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017 30/01/2017


Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017 01/02/2017

Dissolved Aluminium # 5.1 37.8 582.9 668.6 55.4 346.2 6.9 676.5 - 377.6 <1.5 ug/l TM30/PM14

Dissolved Arsenic # <0.9 6.0 <0.9 3.2 5.1 6.6 8.9 3.9 - 4.5 <0.9 ug/l TM30/PM14

Dissolved Barium # 8.0 16.7 6.9 4.0 16.0 <1.8 8.2 2.2 - <1.8 <1.8 ug/l TM30/PM14

Dissolved Cadmium # <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 - <0.03 <0.03 ug/l TM30/PM14

Dissolved Chromium # <0.2 <0.2 0.9 1.0 <0.2 0.9 <0.2 1.1 - 0.9 <0.2 ug/l TM30/PM14

Dissolved Copper # <3 <3 <3 <3 <3 <3 <3 <3 - <3 <3 ug/l TM30/PM14

Dissolved Iron # 38.4 8.3 168.5 150.5 12.6 192.0 73.4 126.6 - 75.8 <4.7 ug/l TM30/PM14

Dissolved Lead # <0.4 <0.4 <0.4 <0.4 <0.4 <0.4 <0.4 <0.4 - <0.4 <0.4 ug/l TM30/PM14

Dissolved Mercury # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 - <0.5 <0.5 ug/l TM30/PM14

Dissolved Molybdenum # 0.2 12.6 0.7 2.6 24.2 10.1 0.8 2.2 - 3.9 <0.2 ug/l TM30/PM14

Dissolved Nickel # 0.7 14.4 1.7 1.6 2.7 1.6 0.3 1.6 - 2.5 <0.2 ug/l TM30/PM14

Dissolved Selenium # <1.2 <1.2 <1.2 <1.2 2.4 4.6 <1.2 <1.2 - <1.2 <1.2 ug/l TM30/PM14

Dissolved Zinc # 5.0 4.6 6.1 4.8 6.0 4.4 7.2 4.2 - 7.1 <1.5 ug/l TM30/PM14

PAH MS

Naphthalene - <0.1 <0.1 <0.1 - - - <0.1 - - <0.1 ug/l TM4/PM30

Acenaphthylene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Acenaphthene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Fluorene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Phenanthrene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Anthracene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Fluoranthene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Pyrene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Benzo(a)anthracene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Chrysene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Benzo(bk)fluoranthene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Benzo(a)pyrene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Indeno(123cd)pyrene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Dibenzo(ah)anthracene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Benzo(ghi)perylene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

PAH 16 Total - <0.1 <0.1 <0.1 - - - <0.1 - - <0.1 ug/l TM4/PM30

Benzo(b)fluoranthene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

Benzo(k)fluoranthene - <0.01 <0.01 <0.01 - - - <0.01 - - <0.01 ug/l TM4/PM30

PAH Surrogate % Recovery - 71 76 74 - - - 74 - - <0 % TM4/PM30

Chloride # 9.1 - - <0.3 - - - <0.3 17.3 - <0.3 mg/l TM38/PM0

Ortho Phosphate as PO4 <0.03 - - <0.03 - - - <0.03 <0.03 - <0.03 mg/l TM38/PM0

Mass of raw test portion - - - - - - - - 0.918 - kg NONE/PM17

Leachant Volume - - - - - - - - 0.068 - l NONE/PM17

Dissolved Chromium III <2 <2 <2 <2 <2 <2 <2 <2 - <2 <2 ug/l NONE/NONE

Hexavalent Chromium <2 <2 <2 <2 <2 <2 <2 <2 - <2 <2 ug/l TM38/PM0

WOP-ADF

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


Reference:


Contact:

JE Job No.: 17/3272

J E Sample No. 27-28 31-32 33-34 35-36

Sample IDWOP-ADF

TP09/17

WOP-ADF

TP10/17

WOP-ADF

TP01/17

WOP-ADF

TP01/17

Depth 1.00 1.00 1.50 3.00

COC No / misc


Sample Date 30/01/2017 30/01/2017 30/01/2017 30/01/2017



Date of Receipt 01/02/2017 01/02/2017 01/02/2017 01/02/2017

Dissolved Aluminium # 722.7 357.8 13.3 242.9 <1.5 ug/l TM30/PM14

Dissolved Arsenic # 1.2 2.6 2.2 8.8 <0.9 ug/l TM30/PM14

Dissolved Barium # 2.4 <1.8 <1.8 3.8 <1.8 ug/l TM30/PM14

Dissolved Cadmium # <0.03 <0.03 <0.03 <0.03 <0.03 ug/l TM30/PM14

Dissolved Chromium # 1.1 1.0 <0.2 0.5 <0.2 ug/l TM30/PM14

Dissolved Copper # <3 <3 <3 <3 <3 ug/l TM30/PM14

Dissolved Iron # 177.7 149.0 11.1 46.2 <4.7 ug/l TM30/PM14

Dissolved Lead # <0.4 <0.4 <0.4 <0.4 <0.4 ug/l TM30/PM14

Dissolved Mercury # <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM30/PM14

Dissolved Molybdenum # 0.4 5.5 <0.2 14.7 <0.2 ug/l TM30/PM14

Dissolved Nickel # 1.3 1.9 <0.2 6.4 <0.2 ug/l TM30/PM14

Dissolved Selenium # <1.2 <1.2 <1.2 <1.2 <1.2 ug/l TM30/PM14

Dissolved Zinc # 4.9 5.3 14.0 4.9 <1.5 ug/l TM30/PM14

PAH MS

Naphthalene <0.1 - 0.5 - <0.1 ug/l TM4/PM30

Acenaphthylene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Acenaphthene 0.01 - 0.02 - <0.01 ug/l TM4/PM30

Fluorene 0.02 - 0.04 - <0.01 ug/l TM4/PM30

Phenanthrene 0.02 - 0.09 - <0.01 ug/l TM4/PM30

Anthracene <0.01 - 0.02 - <0.01 ug/l TM4/PM30

Fluoranthene <0.01 - 0.02 - <0.01 ug/l TM4/PM30

Pyrene <0.01 - 0.02 - <0.01 ug/l TM4/PM30

Benzo(a)anthracene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Chrysene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Benzo(bk)fluoranthene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Benzo(a)pyrene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Indeno(123cd)pyrene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Dibenzo(ah)anthracene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Benzo(ghi)perylene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

PAH 16 Total <0.1 - 0.7 - <0.1 ug/l TM4/PM30

Benzo(b)fluoranthene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

Benzo(k)fluoranthene <0.01 - <0.01 - <0.01 ug/l TM4/PM30

PAH Surrogate % Recovery 76 - 78 - <0 % TM4/PM30

Chloride # - - - 1.5 <0.3 mg/l TM38/PM0

Ortho Phosphate as PO4 - - - <0.03 <0.03 mg/l TM38/PM0

Mass of raw test portion - - - - kg NONE/PM17

Leachant Volume - - - - l NONE/PM17

Dissolved Chromium III <2 <2 <2 <2 <2 ug/l NONE/NONE

Hexavalent Chromium <2 <2 <2 <2 <2 ug/l TM38/PM0

LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239

WOP-ADF

Colm Hurley





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


Reference:

Location:

Contact:

JE Job No.: 17/3272


Sample IDWOP-ADF

TP03/17

WOP-ADF

TP01/17

Depth 1.50 3.00

COC No / misc

Containers V J V J

Sample Date 30/01/2017 30/01/2017


Batch Number 1 1

Date of Receipt 01/02/2017 01/02/2017

SVOC MS

Phenols

2-Chlorophenol # <10 <10 <10 ug/kg TM16/PM8



2,4-Dichlorophenol # <10 <10 <10 ug/kg TM16/PM8

2,4-Dimethylphenol <10 <10 <10 ug/kg TM16/PM8



4-Chloro-3-methylphenol <10 <10 <10 ug/kg TM16/PM8



Pentachlorophenol <10 <10 <10 ug/kg TM16/PM8

Phenol # <10 <10 <10 ug/kg TM16/PM8

PAHs

2-Chloronaphthalene # <10 <10 <10 ug/kg TM16/PM8

2-Methylnaphthalene # <10 <10 <10 ug/kg TM16/PM8

Phthalates

Bis(2-ethylhexyl) phthalate <100 <100 <100 ug/kg TM16/PM8

Butylbenzyl phthalate <100 <100 <100 ug/kg TM16/PM8

Di-n-butyl phthalate <100 <100 <100 ug/kg TM16/PM8

Di-n-Octyl phthalate <100 <100 <100 ug/kg TM16/PM8

Diethyl phthalate <100 <100 <100 ug/kg TM16/PM8

Dimethyl phthalate # <100 <100 <100 ug/kg TM16/PM8

Other SVOCs









4-Bromophenylphenylether # <10 <10 <10 ug/kg TM16/PM8

4-Chloroaniline <10 <10 <10 ug/kg TM16/PM8

4-Chlorophenylphenylether <10 <10 <10 ug/kg TM16/PM8


Azobenzene <10 <10 <10 ug/kg TM16/PM8

Bis(2-chloroethoxy)methane <10 <10 <10 ug/kg TM16/PM8

Bis(2-chloroethyl)ether <10 <10 <10 ug/kg TM16/PM8

Carbazole <10 <10 <10 ug/kg TM16/PM8

Dibenzofuran # <10 <10 <10 ug/kg TM16/PM8

Hexachlorobenzene <10 <10 <10 ug/kg TM16/PM8

Hexachlorobutadiene # <10 <10 <10 ug/kg TM16/PM8

Hexachlorocyclopentadiene <10 <10 <10 ug/kg TM16/PM8

Hexachloroethane <10 <10 <10 ug/kg TM16/PM8

Isophorone # <10 <10 <10 ug/kg TM16/PM8

N-nitrosodi-n-propylamine # <10 <10 <10 ug/kg TM16/PM8

Nitrobenzene # <10 <10 <10 ug/kg TM16/PM8

Surrogate Recovery 2-Fluorobiphenyl 63SV

44SV <0 % TM16/PM8

Surrogate Recovery p-Terphenyl-d14 84 80 <0 % TM16/PM8

WOP-ADF

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


Reference:

Location:

Contact:

JE Job No.: 17/3272


Sample IDWOP-ADF

TP03/17

WOP-ADF

TP01/17

Depth 1.50 3.00

COC No / misc

Containers V J V J

Sample Date 30/01/2017 30/01/2017


Batch Number 1 1

Date of Receipt 01/02/2017 01/02/2017

VOC MS

Dichlorodifluoromethane <2 <2 <2 ug/kg TM15/PM10

Methyl Tertiary Butyl Ether # <2 <2 <2 ug/kg TM15/PM10

Chloromethane # <3 <3 <3 ug/kg TM15/PM10

Vinyl Chloride <2 <2 <2 ug/kg TM15_A/PM10

Bromomethane <1 <1 <1 ug/kg TM15/PM10

Chloroethane # <2 <2 <2 ug/kg TM15/PM10

Trichlorofluoromethane # <2 <2 <2 ug/kg TM15/PM10

1,1-Dichloroethene (1,1 DCE) # <6 <6 <6 ug/kg TM15/PM10

Dichloromethane (DCM) # <30 <30 <30 ug/kg TM15/PM10

trans-1-2-Dichloroethene # <3 <3 <3 ug/kg TM15/PM10

1,1-Dichloroethane # <3 <3 <3 ug/kg TM15/PM10

cis-1-2-Dichloroethene # <3 <3 <3 ug/kg TM15/PM10

2,2-Dichloropropane <4 <4 <4 ug/kg TM15/PM10

Bromochloromethane # <3 <3 <3 ug/kg TM15/PM10

Chloroform # <3 <3 <3 ug/kg TM15/PM10

1,1,1-Trichloroethane # <3 <3 <3 ug/kg TM15/PM10

1,1-Dichloropropene # <3 <3 <3 ug/kg TM15/PM10

Carbon tetrachloride # <4 <4 <4 ug/kg TM15/PM10

1,2-Dichloroethane # <4 <4 <4 ug/kg TM15/PM10

Benzene # <3 <3 <3 ug/kg TM15/PM10

Trichloroethene (TCE) # <3 <3 <3 ug/kg TM15/PM10

1,2-Dichloropropane # <6 <6 <6 ug/kg TM15/PM10

Dibromomethane # <3 <3 <3 ug/kg TM15/PM10

Bromodichloromethane # <3 <3 <3 ug/kg TM15/PM10

cis-1-3-Dichloropropene <4 <4 <4 ug/kg TM15/PM10

Toluene # <3 <3 <3 ug/kg TM15/PM10

trans-1-3-Dichloropropene <3 <3 <3 ug/kg TM15/PM10

1,1,2-Trichloroethane # <3 <3 <3 ug/kg TM15/PM10

Tetrachloroethene (PCE) # <3 <3 <3 ug/kg TM15/PM10

1,3-Dichloropropane # <3 <3 <3 ug/kg TM15/PM10

Dibromochloromethane # <3 <3 <3 ug/kg TM15/PM10

1,2-Dibromoethane # <3 <3 <3 ug/kg TM15/PM10

Chlorobenzene # <3 <3 <3 ug/kg TM15/PM10

1,1,1,2-Tetrachloroethane <3 <3 <3 ug/kg TM15/PM10

Ethylbenzene # <3 <3 <3 ug/kg TM15/PM10

p/m-Xylene # <5 <5 <5 ug/kg TM15/PM10

o-Xylene # <3 <3 <3 ug/kg TM15/PM10

Styrene <3 <3 <3 ug/kg TM15_A/PM10

Bromoform <3 <3 <3 ug/kg TM15/PM10

Isopropylbenzene # <3 <3 <3 ug/kg TM15/PM10

1,1,2,2-Tetrachloroethane # <3 <3 <3 ug/kg TM15/PM10

Bromobenzene <2 <2 <2 ug/kg TM15/PM10

1,2,3-Trichloropropane # <4 <4 <4 ug/kg TM15/PM10

Propylbenzene # <4 <4 <4 ug/kg TM15/PM10

2-Chlorotoluene <3 <3 <3 ug/kg TM15/PM10

1,3,5-Trimethylbenzene # <3 <3 <3 ug/kg TM15/PM10

4-Chlorotoluene <3 <3 <3 ug/kg TM15/PM10

tert-Butylbenzene # <5 <5 <5 ug/kg TM15/PM10

1,2,4-Trimethylbenzene # <6 <6 <6 ug/kg TM15/PM10

sec-Butylbenzene # <4 <4 <4 ug/kg TM15/PM10

4-Isopropyltoluene # <4 <4 <4 ug/kg TM15/PM10

1,3-Dichlorobenzene # <4 <4 <4 ug/kg TM15/PM10


n-Butylbenzene # <4 <4 <4 ug/kg TM15/PM10


1,2-Dibromo-3-chloropropane # <4 <4 <4 ug/kg TM15/PM10


Hexachlorobutadiene <4 <4 <4 ug/kg TM15/PM10

Naphthalene <27 <27 <27 ug/kg TM15/PM10


Surrogate Recovery Toluene D8 99 101 <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 90 88 <0 % TM15/PM10

WOP-ADF

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


J E

Job

No.


No.Analysis Reason




Gemini 16-1239

WOP-ADF

Colm HurleyContact:

Sample ID


Reference:

Location:



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

BLANKS

NOTE






















accredited.

















17/3272

WATERS


blanks.





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No.:

#

SA

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

Dilution required.


Matrix Effect

Blank Sample

Client Sample

Trip Blank Sample

AQC Sample




17/3272



Not applicable






MCERTS accredited.


No Fibres Detected








For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No: 17/3272


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis










by GC-MS. PM8




by GC-MS. PM8





TM5/TM36







PM12/PM16



Trace SPE.

AR Yes

TM5/TM36







PM12/PM16



Trace SPE.

Yes AR Yes







For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No: 17/3272


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis













TM21






























For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No: 17/3272


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis









AD Yes







Yes AD Yes







AR Yes







Yes AR Yes












For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


Zone 3


Deeside

Causeway Geotech

Attention :

Date :

Your reference :

Our reference :

Location :


Status :

Issue :

Colm Hurley

15th March, 2017

1


CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

8 Drumahiskey Road

Bainamore

Ballymoney

Co Antrim

BT53 7QL


Two samples were received for analysis on 2nd March, 2017 of which two were scheduled for analysis. Please find attached our Test Report which

should be read with notes at the end of the report and should include all sections if reproduced. Interpretations and opinions are outside the scope

of any accreditation, and all results relate only to samples supplied.


Bruce Leslie

Project Co-ordinator

Gemini 16-1239

WOP-ADF

2nd March, 2017

Final report

Compiled By:




For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


Reference:


Contact:

JE Job No.: 17/4799


Sample IDWOP-ADF

BH01/17

WOP-ADF

BH03/17

Depth 2.20 4.00

COC No / misc

Containers V J T V J T

Sample Date 22/02/2017 22/02/2017


Batch Number 1 1

Date of Receipt 02/03/2017 02/03/2017

Aluminium 7939 7472 <50 mg/kg TM30/PM15

Arsenic # 3.9 7.3 <0.5 mg/kg TM30/PM15

Barium # 51 43 <1 mg/kg TM30/PM15

Cadmium # 1.2 1.2 <0.1 mg/kg TM30/PM15

Chromium # 24.4 33.7 <0.5 mg/kg TM30/PM15

Copper # 19 17 <1 mg/kg TM30/PM15

Iron 12480 12070 <20 mg/kg TM30/PM15

Lead # 15 13 <5 mg/kg TM30/PM15

Mercury # <0.1 <0.1 <0.1 mg/kg TM30/PM15

Molybdenum # 1.1 2.0 <0.1 mg/kg TM30/PM15

Nickel # 39.3 38.5 <0.7 mg/kg TM30/PM15

Selenium # <1 <1 <1 mg/kg TM30/PM15

Zinc # 86 75 <5 mg/kg TM30/PM15

Natural Moisture Content 26.2 26.3 <0.1 % PM4/PM0

Ammoniacal Nitrogen as N 10.6 - <0.6 mg/kg TM38/PM20

Chloride # 18 - <2 mg/kg TM38/PM20

Hexavalent Chromium # <0.3 <0.3 <0.3 mg/kg TM38/PM20

Ortho Phosphate as PO4 <0.3 - <0.3 mg/kg TM38/PM20

Sulphate as SO4 (2:1 Ext) # 0.0248 - <0.0015 g/l TM38/PM20

Chromium III 24.4 33.7 <0.5 mg/kg NONE/NONE

Organic Matter 1.1 - <0.2 % TM21/PM24

WOP-ADF

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


Reference:


Contact:

JE Job No.: 17/4799


Sample IDWOP-ADF

BH01/17

WOP-ADF

BH03/17

Depth 2.20 4.00

COC No / misc

Containers V J T V J T

Sample Date 22/02/2017 22/02/2017


Batch Number 1 1

Date of Receipt 02/03/2017 02/03/2017

Dissolved Aluminium # 21.0 25.2 <1.5 ug/l TM30/PM14

Dissolved Arsenic # <0.9 <0.9 <0.9 ug/l TM30/PM14

Dissolved Barium # 16.4 3.8 <1.8 ug/l TM30/PM14

Dissolved Cadmium # <0.03 <0.03 <0.03 ug/l TM30/PM14

Dissolved Chromium # <0.2 <0.2 <0.2 ug/l TM30/PM14

Dissolved Copper # <3 <3 <3 ug/l TM30/PM14

Dissolved Iron # <4.7 <4.7 <4.7 ug/l TM30/PM14

Dissolved Lead # <0.4 <0.4 <0.4 ug/l TM30/PM14

Dissolved Mercury # <0.5 <0.5 <0.5 ug/l TM30/PM14

Dissolved Molybdenum # 12.0 15.8 <0.2 ug/l TM30/PM14

Dissolved Nickel # 4.0 12.0 <0.2 ug/l TM30/PM14

Dissolved Selenium # <1.2 <1.2 <1.2 ug/l TM30/PM14

Dissolved Zinc # <1.5 <1.5 <1.5 ug/l TM30/PM14

Chloride # <0.3 - <0.3 mg/l TM38/PM0

Ortho Phosphate as PO4 0.06 - <0.03 mg/l TM38/PM0

Dissolved Chromium III <0.002 <0.002 <0.002 mg/l NONE/NONE

Hexavalent Chromium <0.002 <0.002 <0.002 mg/l TM38/PM0

WOP-ADF

Colm Hurley



LOD/LOR UnitsMethod

No.


Causeway Geotech

Gemini 16-1239



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42


J E

Job

No.


No.Analysis Reason




Gemini 16-1239

WOP-ADF

Colm HurleyContact:

Sample ID


Reference:

Location:



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

BLANKS

NOTE







accredited.










The calculation of Pyrite content assumes that all oxidisable sulphides present in the sample are pyrite. This may not be the case. The calculation

may be an overesitimate when other sulphides such as Barite (Barium Sulphate) are present.


blanks.

























17/4799

WATERS



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No.:

#

SA

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

Matrix Effect

Blank Sample

Client Sample





17/4799



Not applicable


Dilution required.




No Fibres Detected




Trip Blank Sample

AQC Sample



MCERTS accredited.





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No: 17/4799


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis





TM21




























AD Yes







Yes AD Yes



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:42

JE Job No: 17/4799


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis







AR Yes







Yes AR Yes






For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

181

Appendix 5 Groundwater Analytical Results

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

Client Name: Report : Liquid Report : Liquid

Reference:

Location:

Liquids/products: V=40ml vial, G=glass bottle, P=plastic bottle Liquids/products: V=40ml vial, G=glass bottle, P=plastic bottle

JE Job No.: 17/8629 H=H2SO4, Z=ZnAc, N=NaOH, HN=HN03 17/8629 H=H2SO4, Z=ZnAc, N=NaOH, HN=HN03

J E Sample No. 1-8 9-16 17-26 27-34 35-42 51-58 59-66 67-74 75-82 83-92 93-102 103-110 119-126 127-134 NOTES

Sample ID WOP BH02/17 WOP BH04/17 WOP BH05/17 WOP BH06/17 WOP BH09/17WOP-PS-

GW1WOP-PS-GW2

WOP_ADF

BH01/17

WOP_ADF

BH02/17

WOP-ADF

BH03/17

WOP ADF

GW3

WOP ADF

GW4

WOP ADF

GW5

WOP ADF

GW6

Containers V H HN Z P G V H HN Z P G V H HN Z P G BC V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G BC V H HN Z P G BC V H HN Z P G V H HN Z P G V H HN Z P G

Sample Date 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017

Sample Type Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water

Batch Number 1 1 1 1 1 1 1 1 1 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

GW Regulations GTV IGV SW EQS checked standards checked results incl units

Metals Dissolved Aluminium # 150 291 20 661 1083 20 20 20 20 20 20 20 20 20 20 When 20<20 <20 ug/l TM30/PM14

Dissolved Arsenic # 7.5 2.5 2.8 5.3 6.7 2.5 2.5 2.5 3 19.8 19.1 2.5 2.5 49.5 14.1 2.5 = <2.5 <2.5 ug/l TM30/PM14

Dissolved Boron 1000 <12 52 18 105 79 27 80 <12 <12 <12 <12 <12 <12 <12 <12 ug/l TM30/PM14

Dissolved Cadmium # 3.75 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 = <0.5 <0.5 ug/l TM30/PM14

Dissolved Calcium # 200000 186.3 143 101.1 54 61.2 148 115.6 98.2 127.7 143.5 95.4 92.7 132 117.4 <0.2 mg/l TM30/PM14

Total Dissolved Chromium # 37.5 1.5 1.5 11.3 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 = <1.5 <1.5 ug/l TM30/PM14

Dissolved Copper # 1500 <7 <7 <7 <7 <7 <7 18 <7 <7 <7 <7 <7 <7 <7 <7 ug/l TM30/PM14

Total Dissolved Iron # 200 20 7588 21 69 20 242 1800 2602 3615 2803 1203 2691 9159 5720 20=<20 <20 ug/l TM30/PM14

Dissolved Lead # 18.75 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 ug/l TM30/PM14

Dissolved Magnesium # 50000 <0.1 15.2 0.4 <0.1 17.1 15.1 20.4 10.1 4.5 3.5 4.7 2.2 1.9 5 <0.1 mg/l TM30/PM14

Dissolved Manganese # 50 2 928 2 2 239 823 203 3672 877 168 86 95 56 110 2=<2 <2 ug/l TM30/PM14

Dissolved Mercury # 0.75 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 ug/l TM30/PM14

Dissolved Molybdenum # 65 11 95 109 51 <2 5 4 7 <2 <2 <2 4 <2 <2 ug/l TM30/PM14

Dissolved Nickel # 15 2 9 4 2 2 2 2 2 15 6 2 2 20 2 2 = <2 <2 ug/l TM30/PM14

Dissolved Potassium # 5000 88.5 11.8 42.9 63.7 4.9 0.8 19.9 1.4 1.5 1.7 0.7 10.5 1.6 1.5 <0.1 mg/l TM30/PM14

Dissolved Selenium # <3 <3 5 <3 <3 <3 <3 <3 <3 <3 <3 <3 <3 <3 <3 ug/l TM30/PM14

Dissolved Sodium # 150 160.8 96.1 105 193.6 37.2 11 80.4 9 9.9 10.2 7.9 26.7 8.5 7.4 <0.1 mg/l TM30/PM14

Dissolved Zinc # 100 <3 <3 <3 <3 <3 7 <3 <3 <3 4 <3 <3 <3 <3 <3 ug/l TM30/PM14

PAH MS Naphthalene # 1 1.2 <0.1

B<0.1

B<0.1

B<0.1

B<0.1

B<0.1

B<0.1

B<0.1

B<0.1

B<0.1

B<0.1

B0.1

B<0.1

B0.1

B <0.1 ug/l TM4/PM30

Acenaphthylene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Acenaphthene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 0.061 <0.013 <0.013 ug/l TM4/PM30

Fluorene # <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 0.056 <0.014 <0.014 ug/l TM4/PM30

Phenanthrene # 0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 0.03 <0.011 <0.011 ug/l TM4/PM30

Anthracene # 10000 0.1 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 0.019 <0.013 <0.013 ug/l TM4/PM30

Fluoranthene # 1 0.1 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 ug/l TM4/PM30

Pyrene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Benzo(a)anthracene # <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 ug/l TM4/PM30

Chrysene # <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Benzo(bk)fluoranthene # <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 ug/l TM4/PM30

Benzo(a)pyrene # <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 ug/l TM4/PM30

Indeno(123cd)pyrene # 0.05 0.002 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Dibenzo(ah)anthracene # <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(ghi)perylene # 0.05 0.002 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Coronene <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ug/l TM4/PM30

PAH 17 Total <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 ug/l TM4/PM30

Benzo(b)fluoranthene 0.05 0.002 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(k)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

PAH Surrogate % Recovery 90 92 92 94 89 96 89 91 93 95 95 92 90 92 <0 % TM4/PM30

Methyl Tertiary Butyl Ether # <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 - - - <0.1 ug/l TM15/PM10

Benzene # 0.75 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 - - - <0.5 ug/l TM15/PM10

Toluene # 10 10 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 - - - <5 ug/l TM15/PM10

Ethylbenzene # 10 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 - - - <1 ug/l TM15/PM10

p/m-Xylene # 10 <2 <2 <2 <2 <2 7 <2 <2 <2 <2 <2 - - - <2 ug/l TM15/PM10

o-Xylene # 10 <1 <1 <1 <1 <1 3 <1 <1 <1 <1 <1 - - - <1 ug/l TM15/PM10

Surrogate Recovery Toluene D8 113 115 104 118 124 124 114 104 109 99 106 - - - <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 111 116 114 119 117 118 112 107 99 107 99 - - - <0 % TM15/PM10

Pesticides Aldrin 0.01 - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Standards

ESB Networks

West Offaly Power


ESB Networks

GWM 6557 (Gemini)

West Offaly Power

LOD/LOR UnitsMethod

No.

GWM 6557 (Gemini)

QF-PM 3.1.2 v11

Please include all sections of this report if it is reproduced


For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

Organochlorine Pesticides Alpha-HCH (BHC) - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Beta-HCH (BHC) - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Delta-HCH (BHC) - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Dieldrin 0.075 - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Endosulphan I - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Endosulphan II - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Endosulphan sulphate - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Endrin - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Gamma-HCH (BHC) - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Heptachlor - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Heptachlor Epoxide - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

o,p'-Methoxychlor - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

p,p'-DDE - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

p,p'-DDT 0.01 - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

p,p'-Methoxychlor - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

p,p'-TDE - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Organophosphorus Pesticides Azinphos methyl - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Diazinon - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Dichlorvos 0.001 - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Disulfoton - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Ethion - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Ethyl Parathion (Parathion) - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Fenitrothion - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Malathion - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Methyl Parathion - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Mevinphos - - <0.01 - - - - - - <0.01 <0.01 - - - <0.01 ug/l TM149/PM30

Benazolin - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Bentazone 0.075 - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Bromoxynil 5 - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Clopyralid - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

4 - CPA - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

2,4 - D - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

2,4 - DB - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Dicamba - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Dichloroprop 100 - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Diclofop - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Fenoprop - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Flamprop - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Flamprop – isopropyl - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Ioxynil - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

MCPA 0.075 - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

MCPB - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Mecoprop 0.075 10 - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Picloram - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Pentachlorophenol 2 - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

2,4,5 - T - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

2,3,6 - TBA - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

Triclopyr - - <0.1 - - - - - - <0.1 <0.1 - - - <0.1 ug/l TM42/PM30

TPH CWG >C5-C6 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

Aliphatics >C6-C8 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C8-C10 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C10-C12 # <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 ug/l TM5/PM30

>C12-C16 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>C16-C21 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>C21-C35 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

Total aliphatics C5-35 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Aromatics >C5-EC7 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC7-EC8 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC8-EC10 # <10 <10 <10 <10 <10 15 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC10-EC12 # <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 ug/l TM5/PM30

>EC12-EC16 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>EC16-EC21 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>EC21-EC35 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

Total aromatics C5-35 # <10 <10 <10 <10 <10 15 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Total aliphatics and aromatics(C5-35) # <10 <10 <10 <10 <10 15 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Phenols Total Phenols HPLC <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 - <0.1 <0.1 <0.1 mg/l TM26/PM0

Other Sulphate as SO4 # 187.5 120.9 191 310.9 108.3 162.8 41.3 248.6 1.1 <0.5 18.6 <0.5 <0.5 <0.5 <0.5 <0.5 mg/l TM38/PM0

Chloride # 187.5 53.5 43.8 41.4 83.6 27.9 16.3 50.5 11.5 13.2 47.3 15.3 38.4 11 9.9 <0.3 mg/l TM38/PM0

Nitrate as NO3 # 37.5 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.2 = <0.02 <0.2 mg/l TM38/PM0

QF-PM 3.1.2 v11



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

Nitrite as NO2 # 375 <0.02 0.03 <0.02 <0.02 0.14 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 mg/l TM38/PM0

Ortho Phosphate as P # 30 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04 <0.03 mg/l TM38/PM0

Ammoniacal Nitrogen as N # 0.175 3.69 2.44 6.72 21.29 1.78 0.04 9.81 2.07 9.22 7.52 2.03 3.17 7.95 4.71 <0.03 mg/l TM38/PM0

Ammoniacal Nitrogen as NH3 # 4.48 2.96 8.17 25.89 2.16 0.05 11.92 2.52 11.21 9.14 2.46 3.85 9.67 5.72 <0.03 mg/l TM38/PM0

Hexavalent Chromium <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 mg/l TM38/PM0

Total Dissolved Chromium III <6 <6 11 <6 <6 <6 <6 <6 <6 <6 <6 <6 <6 <6 <6 ug/l NONE/NONE

Sulphide <10 <10 <10 20 <10 <10 20 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM106/PM0

COD (Settled) # - - 40 - - - - - - 21 48 - - - <7 mg/l TM57/PM0

Total Coliforms* - - <1 - - - - - - <1 <1 - - - CFU/100ml Subcontracted

Produced: Oonagh Duffy

Checked: Keelin Timoney


QF-PM 3.1.2 v11



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

185

Appendix 6.Groundwater Laboratory Results

For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Zone 3


Deeside

ESB Networks

Attention :

Date :

Your reference :

Our reference :

Location :


Status :

Issue :

Anne-Marie Casey

26th May, 2017

1


CH5 2UA

Tel: +44 (0) 1244 833780

Fax: +44 (0) 1244 833781

Newcastle West

Co Limerick

Ireland


Sixteen samples were received for analysis on 15th May, 2017 of which sixteen were scheduled for analysis. Please find attached our Test Report




Paul Boden BSc

Project Manager

GWM 6557 (Gemini)

West Offaly Power

15th May, 2017

Final report

Compiled By:




For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

Client Name: Report : Liquid

Reference:

Location:

Contact: Liquids/products: V=40ml vial, G=glass bottle, P=plastic bottle

JE Job No.: 17/8629 H=H2SO4, Z=ZnAc, N=NaOH, HN=HN03

J E Sample No. 1-8 9-16 17-26 27-34 35-42 43-50 51-58 59-66 67-74 75-82

Sample ID WOP BH02/17 WOP BH04/17 WOP BH05/17 WOP BH06/17 WOP BH09/17WOP BH09/17

(DUP)

WOP-PS-

GW1

WOP-PS-

GW2WOP BH01/17 WOP BH02/17

Depth

COC No / misc

Containers V H HN Z P G V H HN Z P G V H HN Z P G BC V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G

Sample Date 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 10/05/2017 10/05/2017 10/05/2017

Sample Type Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water

Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Dissolved Aluminium # 291 <20 661 1083 <20 <20 <20 <20 <20 <20 <20 ug/l TM30/PM14

Dissolved Arsenic # <2.5 2.8 5.3 6.7 <2.5 <2.5 <2.5 <2.5 3.0 19.8 <2.5 ug/l TM30/PM14

Dissolved Boron <12 52 18 105 79 83 27 80 <12 <12 <12 ug/l TM30/PM14

Dissolved Cadmium # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM30/PM14

Dissolved Calcium # 186.3 143.0 101.1 54.0 61.2 63.0 148.0 115.6 98.2 127.7 <0.2 mg/l TM30/PM14

Total Dissolved Chromium # <1.5 <1.5 11.3 <1.5 <1.5 <1.5 <1.5 <1.5 <1.5 <1.5 <1.5 ug/l TM30/PM14

Dissolved Copper # <7 <7 <7 <7 <7 <7 <7 18 <7 <7 <7 ug/l TM30/PM14

Total Dissolved Iron # <20 7588 21 69 <20 <20 242 1800 2602 3615 <20 ug/l TM30/PM14

Dissolved Lead # <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 ug/l TM30/PM14

Dissolved Magnesium # <0.1 15.2 0.4 <0.1 17.1 17.8 15.1 20.4 10.1 4.5 <0.1 mg/l TM30/PM14

Dissolved Manganese # <2 928 <2 <2 239 233 823 203 3672 877 <2 ug/l TM30/PM14

Dissolved Mercury # <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 ug/l TM30/PM14

Dissolved Molybdenum # 65 11 95 109 51 51 <2 5 4 7 <2 ug/l TM30/PM14

Dissolved Nickel # <2 9 4 <2 <2 <2 <2 <2 2 15 <2 ug/l TM30/PM14

Dissolved Potassium # 88.5 11.8 42.9 63.7 4.9 5.0 0.8 19.9 1.4 1.5 <0.1 mg/l TM30/PM14

Dissolved Selenium # <3 <3 5 <3 <3 <3 <3 <3 <3 <3 <3 ug/l TM30/PM14

Dissolved Sodium # 160.8 96.1 105.0 193.6 37.2 38.8 11.0 80.4 9.0 9.9 <0.1 mg/l TM30/PM14

Dissolved Zinc # <3 <3 <3 <3 <3 <3 7 <3 <3 <3 <3 ug/l TM30/PM14

PAH MS

Naphthalene #

<0.1B

<0.1B

<0.1B

<0.1B

<0.1B

<0.1B

<0.1B

<0.1B

<0.1B

<0.1B <0.1 ug/l TM4/PM30

Acenaphthylene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Acenaphthene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Fluorene # <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 <0.014 ug/l TM4/PM30

Phenanthrene # 0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Anthracene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Fluoranthene # <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 ug/l TM4/PM30

Pyrene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Benzo(a)anthracene # <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 ug/l TM4/PM30

Chrysene # <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Benzo(bk)fluoranthene # <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 ug/l TM4/PM30

Benzo(a)pyrene # <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 ug/l TM4/PM30

Indeno(123cd)pyrene # <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Dibenzo(ah)anthracene # <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(ghi)perylene # <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Coronene <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ug/l TM4/PM30

PAH 17 Total <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 ug/l TM4/PM30

Benzo(b)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(k)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

PAH Surrogate % Recovery 90 92 92 94 89 93 96 89 91 93 <0 % TM4/PM30

Methyl Tertiary Butyl Ether # <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ug/l TM15/PM10

Benzene # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM15/PM10

Toluene # <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 ug/l TM15/PM10

West Offaly Power

Anne-Marie Casey



LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Reference:

Location:



J E Sample No. 1-8 9-16 17-26 27-34 35-42 43-50 51-58 59-66 67-74 75-82


(DUP)

WOP-PS-

GW1

WOP-PS-


Depth

COC No / misc


Sample Date 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 10/05/2017 10/05/2017 10/05/2017


Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Ethylbenzene # <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 ug/l TM15/PM10

p/m-Xylene # <2 <2 <2 <2 <2 <2 7 <2 <2 <2 <2 ug/l TM15/PM10

o-Xylene # <1 <1 <1 <1 <1 <1 3 <1 <1 <1 <1 ug/l TM15/PM10

Surrogate Recovery Toluene D8 113 115 104 118 124 129 124 114 104 109 <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 111 116 114 119 117 117 118 112 107 99 <0 % TM15/PM10

Pesticides

Organochlorine Pesticides

Aldrin - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Alpha-HCH (BHC) - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Beta-HCH (BHC) - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Delta-HCH (BHC) - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Dieldrin - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Endosulphan I - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Endosulphan II - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Endosulphan sulphate - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Endrin - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Gamma-HCH (BHC) - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Heptachlor - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Heptachlor Epoxide - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

o,p'-Methoxychlor - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

p,p'-DDE - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

p,p'-DDT - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

p,p'-Methoxychlor - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

p,p'-TDE - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Organophosphorus Pesticides

Azinphos methyl - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Diazinon - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Dichlorvos - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Disulfoton - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Ethion - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Ethyl Parathion (Parathion) - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Fenitrothion - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Malathion - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Methyl Parathion - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Mevinphos - - <0.01 - - - - - - - <0.01 ug/l TM149/PM30

Benazolin - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Bentazone - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Bromoxynil - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Clopyralid - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

4 - CPA - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

2,4 - D - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

2,4 - DB - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)

West Offaly Power

Anne-Marie Casey





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Reference:

Location:



J E Sample No. 1-8 9-16 17-26 27-34 35-42 43-50 51-58 59-66 67-74 75-82


(DUP)

WOP-PS-

GW1

WOP-PS-


Depth

COC No / misc


Sample Date 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 10/05/2017 10/05/2017 10/05/2017


Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Dicamba - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Dichloroprop - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Diclofop - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Fenoprop - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Flamprop - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Flamprop – isopropyl - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Ioxynil - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

MCPA - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

MCPB - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Mecoprop - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Picloram - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Pentachlorophenol - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

2,4,5 - T - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

2,3,6 - TBA - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

Triclopyr - - <0.1 - - - - - - - <0.1 ug/l TM42/PM30

TPH CWG

Aliphatics

>C5-C6 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C6-C8 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C8-C10 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C10-C12 # <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 ug/l TM5/PM30

>C12-C16 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>C16-C21 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>C21-C35 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

Total aliphatics C5-35 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Aromatics

>C5-EC7 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC7-EC8 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC8-EC10 # <10 <10 <10 <10 <10 <10 15 <10 <10 <10 <10 ug/l TM36/PM12

>EC10-EC12 # <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 <5 ug/l TM5/PM30

>EC12-EC16 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>EC16-EC21 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>EC21-EC35 # <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

Total aromatics C5-35 # <10 <10 <10 <10 <10 <10 15 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Total aliphatics and aromatics(C5-35) # <10 <10 <10 <10 <10 <10 15 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Total Phenols HPLC <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/l TM26/PM0

Sulphate as SO4 # 120.9 191.0 310.9 108.3 162.8 162.0 41.3 248.6 1.1 <0.5 <0.5 mg/l TM38/PM0

Chloride # 53.5 43.8 41.4 83.6 27.9 27.8 16.3 50.5 11.5 13.2 <0.3 mg/l TM38/PM0

Nitrate as NO3 # <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 mg/l TM38/PM0

Nitrite as NO2 # <0.02 0.03 <0.02 <0.02 0.14 0.21 <0.02 <0.02 <0.02 <0.02 <0.02 mg/l TM38/PM0

Ortho Phosphate as P # <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 mg/l TM38/PM0

West Offaly Power

Anne-Marie Casey



LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Reference:

Location:



J E Sample No. 1-8 9-16 17-26 27-34 35-42 43-50 51-58 59-66 67-74 75-82


(DUP)

WOP-PS-

GW1

WOP-PS-


Depth

COC No / misc


Sample Date 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 11/05/2017 10/05/2017 10/05/2017 10/05/2017


Batch Number 1 1 1 1 1 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Ammoniacal Nitrogen as N # 3.69 2.44 6.72 21.29 1.78 1.76 0.04 9.81 2.07 9.22 <0.03 mg/l TM38/PM0

Ammoniacal Nitrogen as NH3 # 4.48 2.96 8.17 25.89 2.16 2.14 0.05 11.92 2.52 11.21 <0.03 mg/l TM38/PM0

Hexavalent Chromium <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 mg/l TM38/PM0

Total Dissolved Chromium III <6 <6 11 <6 <6 <6 <6 <6 <6 <6 <6 ug/l NONE/NONE

Sulphide <10 <10 <10 20 <10 <10 <10 20 <10 <10 <10 ug/l TM106/PM0

COD (Settled) # - - 40 - - - - - - - <7 mg/l TM57/PM0

Total Coliforms* - - <1 - - - - - - - CFU/100ml Subcontracted

LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)

West Offaly Power

Anne-Marie Casey





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Reference:

Location:



J E Sample No. 83-92 93-102 103-110 111-118 119-126 127-134

Sample ID WOP BH03/17WOP ADF

GW3

WOP ADF

GW4

WOP ADF

GW4(DUP)

WOP ADF

GW5

WOP ADF

GW6

Depth

COC No / misc

Containers V H HN Z P G BC V H HN Z P G BC V H HN Z P G V H HN Z P G V H HN Z P G V H HN Z P G

Sample Date 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017

Sample Type Ground Water Ground Water Ground Water Ground Water Ground Water Ground Water

Batch Number 1 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Dissolved Aluminium # <20 <20 <20 <20 <20 <20 <20 ug/l TM30/PM14

Dissolved Arsenic # 19.1 <2.5 <2.5 <2.5 49.5 14.1 <2.5 ug/l TM30/PM14

Dissolved Boron <12 <12 <12 <12 <12 <12 <12 ug/l TM30/PM14

Dissolved Cadmium # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM30/PM14

Dissolved Calcium # 143.5 95.4 92.7 95.1 132.0 117.4 <0.2 mg/l TM30/PM14

Total Dissolved Chromium # <1.5 <1.5 <1.5 <1.5 <1.5 <1.5 <1.5 ug/l TM30/PM14

Dissolved Copper # <7 <7 <7 <7 <7 <7 <7 ug/l TM30/PM14

Total Dissolved Iron # 2803 1203 2691 2617 9159 5720 <20 ug/l TM30/PM14

Dissolved Lead # <5 <5 <5 <5 <5 <5 <5 ug/l TM30/PM14

Dissolved Magnesium # 3.5 4.7 2.2 2.2 1.9 5.0 <0.1 mg/l TM30/PM14

Dissolved Manganese # 168 86 95 93 56 110 <2 ug/l TM30/PM14

Dissolved Mercury # <1 <1 <1 <1 <1 <1 <1 ug/l TM30/PM14

Dissolved Molybdenum # <2 <2 <2 <2 4 <2 <2 ug/l TM30/PM14

Dissolved Nickel # 6 <2 <2 <2 20 <2 <2 ug/l TM30/PM14

Dissolved Potassium # 1.7 0.7 10.5 11.5 1.6 1.5 <0.1 mg/l TM30/PM14

Dissolved Selenium # <3 <3 <3 <3 <3 <3 <3 ug/l TM30/PM14

Dissolved Sodium # 10.2 7.9 26.7 27.2 8.5 7.4 <0.1 mg/l TM30/PM14

Dissolved Zinc # 4 <3 <3 <3 <3 <3 <3 ug/l TM30/PM14

PAH MS

Naphthalene #

<0.1B

<0.1B

0.1B

0.1B

<0.1B

0.1B <0.1 ug/l TM4/PM30

Acenaphthylene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Acenaphthene # <0.013 <0.013 <0.013 <0.013 0.061 <0.013 <0.013 ug/l TM4/PM30

Fluorene # <0.014 <0.014 <0.014 <0.014 0.056 <0.014 <0.014 ug/l TM4/PM30

Phenanthrene # <0.011 <0.011 <0.011 <0.011 0.030 <0.011 <0.011 ug/l TM4/PM30

Anthracene # <0.013 <0.013 <0.013 <0.013 0.019 <0.013 <0.013 ug/l TM4/PM30

Fluoranthene # <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 <0.012 ug/l TM4/PM30

Pyrene # <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 <0.013 ug/l TM4/PM30

Benzo(a)anthracene # <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 <0.015 ug/l TM4/PM30

Chrysene # <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Benzo(bk)fluoranthene # <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 <0.018 ug/l TM4/PM30

Benzo(a)pyrene # <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 <0.016 ug/l TM4/PM30

Indeno(123cd)pyrene # <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Dibenzo(ah)anthracene # <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(ghi)perylene # <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 <0.011 ug/l TM4/PM30

Coronene <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ug/l TM4/PM30

PAH 17 Total <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 <0.295 ug/l TM4/PM30

Benzo(b)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

Benzo(k)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 ug/l TM4/PM30

PAH Surrogate % Recovery 95 95 92 95 90 92 <0 % TM4/PM30

Methyl Tertiary Butyl Ether # <0.1 <0.1 - - - - <0.1 ug/l TM15/PM10

Benzene # <0.5 <0.5 - - - - <0.5 ug/l TM15/PM10

Toluene # <5 <5 - - - - <5 ug/l TM15/PM10

West Offaly Power

Anne-Marie Casey



LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Reference:

Location:



J E Sample No. 83-92 93-102 103-110 111-118 119-126 127-134


GW3

WOP ADF

GW4

WOP ADF

GW4(DUP)

WOP ADF

GW5

WOP ADF

GW6

Depth

COC No / misc


Sample Date 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017



Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Ethylbenzene # <1 <1 - - - - <1 ug/l TM15/PM10

p/m-Xylene # <2 <2 - - - - <2 ug/l TM15/PM10

o-Xylene # <1 <1 - - - - <1 ug/l TM15/PM10

Surrogate Recovery Toluene D8 99 106 - - - - <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 107 99 - - - - <0 % TM15/PM10

Pesticides

Organochlorine Pesticides

Aldrin <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Alpha-HCH (BHC) <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Beta-HCH (BHC) <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Delta-HCH (BHC) <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Dieldrin <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Endosulphan I <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Endosulphan II <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Endosulphan sulphate <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Endrin <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Gamma-HCH (BHC) <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Heptachlor <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Heptachlor Epoxide <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

o,p'-Methoxychlor <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

p,p'-DDE <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

p,p'-DDT <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

p,p'-Methoxychlor <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

p,p'-TDE <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Organophosphorus Pesticides

Azinphos methyl <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Diazinon <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Dichlorvos <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Disulfoton <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Ethion <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Ethyl Parathion (Parathion) <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Fenitrothion <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Malathion <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Methyl Parathion <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Mevinphos <0.01 <0.01 - - - - <0.01 ug/l TM149/PM30

Benazolin <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Bentazone <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Bromoxynil <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Clopyralid <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

4 - CPA <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

2,4 - D <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

2,4 - DB <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)

West Offaly Power

Anne-Marie Casey





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Reference:

Location:



J E Sample No. 83-92 93-102 103-110 111-118 119-126 127-134


GW3

WOP ADF

GW4

WOP ADF

GW4(DUP)

WOP ADF

GW5

WOP ADF

GW6

Depth

COC No / misc


Sample Date 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017



Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Dicamba <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Dichloroprop <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Diclofop <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Fenoprop <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Flamprop <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Flamprop – isopropyl <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Ioxynil <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

MCPA <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

MCPB <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Mecoprop <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Picloram <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Pentachlorophenol <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

2,4,5 - T <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

2,3,6 - TBA <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

Triclopyr <0.1 <0.1 - - - - <0.1 ug/l TM42/PM30

TPH CWG

Aliphatics

>C5-C6 # <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C6-C8 # <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C8-C10 # <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>C10-C12 # <5 <5 <5 <5 <5 <5 <5 ug/l TM5/PM30

>C12-C16 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>C16-C21 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>C21-C35 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

Total aliphatics C5-35 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Aromatics

>C5-EC7 # <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC7-EC8 # <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC8-EC10 # <10 <10 <10 <10 <10 <10 <10 ug/l TM36/PM12

>EC10-EC12 # <5 <5 <5 <5 <5 <5 <5 ug/l TM5/PM30

>EC12-EC16 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>EC16-EC21 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

>EC21-EC35 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/PM30

Total aromatics C5-35 # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Total aliphatics and aromatics(C5-35) # <10 <10 <10 <10 <10 <10 <10 ug/l TM5/TM36/PM30/PM12

Total Phenols HPLC <0.1 <0.1 - - <0.1 <0.1 <0.1 mg/l TM26/PM0

Sulphate as SO4 # 18.6 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 mg/l TM38/PM0

Chloride # 47.3 15.3 38.4 39.5 11.0 9.9 <0.3 mg/l TM38/PM0

Nitrate as NO3 # <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 mg/l TM38/PM0

Nitrite as NO2 # <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 mg/l TM38/PM0

Ortho Phosphate as P # <0.03 <0.03 <0.03 <0.03 <0.03 0.04 <0.03 mg/l TM38/PM0

West Offaly Power

Anne-Marie Casey



LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


Reference:

Location:



J E Sample No. 83-92 93-102 103-110 111-118 119-126 127-134


GW3

WOP ADF

GW4

WOP ADF

GW4(DUP)

WOP ADF

GW5

WOP ADF

GW6

Depth

COC No / misc


Sample Date 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017 10/05/2017



Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

Ammoniacal Nitrogen as N # 7.52 2.03 3.17 3.13 7.95 4.71 <0.03 mg/l TM38/PM0

Ammoniacal Nitrogen as NH3 # 9.14 2.46 3.85 3.80 9.67 5.72 <0.03 mg/l TM38/PM0

Hexavalent Chromium <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 mg/l TM38/PM0

Total Dissolved Chromium III <6 <6 <6 <6 <6 <6 <6 ug/l NONE/NONE

Sulphide <10 <10 <10 <10 <10 <10 <10 ug/l TM106/PM0

COD (Settled) # 21 48 - - - - <7 mg/l TM57/PM0

Total Coliforms* <1 <1 - - - - CFU/100ml Subcontracted

LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)

West Offaly Power

Anne-Marie Casey





For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

Client Name: SVOC Report : Liquid

Reference:

Location:

Contact:

JE Job No.: 17/8629

J E Sample No. 1-8 17-26 51-58 83-92 93-102

Sample ID WOP BH02/17 WOP BH05/17WOP-PS-

GW1WOP BH03/17

WOP ADF

GW3

Depth

COC No / misc

Containers V H HN Z P G V H HN Z P G BC V H HN Z P G V H HN Z P G BC V H HN Z P G BC

Sample Date 11/05/2017 11/05/2017 11/05/2017 10/05/2017 10/05/2017

Sample Type Ground Water Ground Water Ground Water Ground Water Ground Water

Batch Number 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

SVOC MS

Phenols

2-Chlorophenol # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

2-Methylphenol # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

2-Nitrophenol <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

2,4-Dichlorophenol # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

2,4-Dimethylphenol <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

2,4,5-Trichlorophenol # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

2,4,6-Trichlorophenol <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

4-Chloro-3-methylphenol # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

4-Methylphenol <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

4-Nitrophenol <10 <10 <10 <10 <10 <10 ug/l TM16/PM30

Pentachlorophenol <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Phenol <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

PAHs

2-Chloronaphthalene # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

2-Methylnaphthalene # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Phthalates

Bis(2-ethylhexyl) phthalate <5 <5 <5 <5 <5 <5 ug/l TM16/PM30

Butylbenzyl phthalate <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Di-n-butyl phthalate #

<1.5+ <1.5 <1.5 <1.5 <1.5 <1.5 ug/l TM16/PM30

Di-n-Octyl phthalate <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Diethyl phthalate # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Dimethyl phthalate <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Other SVOCs

1,2-Dichlorobenzene # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

1,2,4-Trichlorobenzene # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30



2-Nitroaniline <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

2,4-Dinitrotoluene # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

2,6-Dinitrotoluene <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

3-Nitroaniline <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

4-Bromophenylphenylether # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

4-Chloroaniline <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

4-Chlorophenylphenylether # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

4-Nitroaniline <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

Azobenzene # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

Bis(2-chloroethoxy)methane # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

Bis(2-chloroethyl)ether # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Carbazole # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

Dibenzofuran # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

Hexachlorobenzene # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Hexachlorobutadiene # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Hexachlorocyclopentadiene <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Hexachloroethane # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Isophorone # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

N-nitrosodi-n-propylamine # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM16/PM30

Nitrobenzene # <1 <1 <1 <1 <1 <1 ug/l TM16/PM30

Surrogate Recovery 2-Fluorobiphenyl 112 102 105 116 102 <0 % TM16/PM30

Surrogate Recovery p-Terphenyl-d14 75 71 72 79 80 <0 % TM16/PM30

West Offaly Power

Anne-Marie Casey



LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

Client Name: VOC Report : Liquid

Reference:

Location:

Contact:

JE Job No.: 17/8629

J E Sample No. 1-8 17-26 51-58 83-92 93-102

Sample ID WOP BH02/17 WOP BH05/17WOP-PS-

GW1WOP BH03/17

WOP ADF

GW3

Depth

COC No / misc

Containers V H HN Z P G V H HN Z P G BC V H HN Z P G V H HN Z P G BC V H HN Z P G BC

Sample Date 11/05/2017 11/05/2017 11/05/2017 10/05/2017 10/05/2017

Sample Type Ground Water Ground Water Ground Water Ground Water Ground Water

Batch Number 1 1 1 1 1

Date of Receipt 15/05/2017 15/05/2017 15/05/2017 15/05/2017 15/05/2017

VOC MS

Dichlorodifluoromethane <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Methyl Tertiary Butyl Ether # <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ug/l TM15/PM10

Chloromethane # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Vinyl Chloride # <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ug/l TM15/PM10

Bromomethane <1 <1 <1 <1 <1 <1 ug/l TM15/PM10

Chloroethane # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Trichlorofluoromethane # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

1,1-Dichloroethene (1,1 DCE) # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Dichloromethane (DCM) # <5 <5 <5 <5 <5 <5 ug/l TM15/PM10

trans-1-2-Dichloroethene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

1,1-Dichloroethane # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

cis-1-2-Dichloroethene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

2,2-Dichloropropane <1 <1 <1 <1 <1 <1 ug/l TM15/PM10

Bromochloromethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Chloroform # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,1,1-Trichloroethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,1-Dichloropropene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Carbon tetrachloride # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,2-Dichloroethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Benzene # <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 ug/l TM15/PM10

Trichloroethene (TCE) # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

1,2-Dichloropropane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Dibromomethane # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Bromodichloromethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

cis-1-3-Dichloropropene <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Toluene # <5 <5 <5 <5 <5 <5 ug/l TM15/PM10

trans-1-3-Dichloropropene <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,1,2-Trichloroethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Tetrachloroethene (PCE) # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

1,3-Dichloropropane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Dibromochloromethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,2-Dibromoethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Chlorobenzene # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,1,1,2-Tetrachloroethane # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Ethylbenzene # <1 <1 <1 <1 <1 <1 ug/l TM15/PM10

p/m-Xylene # <2 <2 7 <2 <2 <2 ug/l TM15/PM10

o-Xylene # <1 <1 3 <1 <1 <1 ug/l TM15/PM10

Styrene <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Bromoform # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

Isopropylbenzene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

1,1,2,2-Tetrachloroethane <4 <4 <4 <4 <4 <4 ug/l TM15/PM10

Bromobenzene # <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,2,3-Trichloropropane # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Propylbenzene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

2-Chlorotoluene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

1,3,5-Trimethylbenzene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

4-Chlorotoluene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

tert-Butylbenzene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

1,2,4-Trimethylbenzene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

sec-Butylbenzene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

4-Isopropyltoluene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10



n-Butylbenzene # <3 <3 <3 <3 <3 <3 ug/l TM15/PM10


1,2-Dibromo-3-chloropropane <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,2,4-Trichlorobenzene <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Hexachlorobutadiene <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Naphthalene <2 <2 <2 <2 <2 <2 ug/l TM15/PM10

1,2,3-Trichlorobenzene <3 <3 <3 <3 <3 <3 ug/l TM15/PM10

Surrogate Recovery Toluene D8 113 104 124 99 106 <0 % TM15/PM10

Surrogate Recovery 4-Bromofluorobenzene 111 114 118 107 99 <0 % TM15/PM10

West Offaly Power

Anne-Marie Casey



LOD/LOR UnitsMethod

No.


ESB Networks

GWM 6557 (Gemini)



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43


J E

Job

No.


No.Analysis Reason




GWM 6557 (Gemini)

West Offaly Power

Anne-Marie CaseyContact:

Sample ID

Client Name: ESB Networks

Reference:

Location:



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

JE Job No.:

SOILS

DEVIATING SAMPLES

SURROGATES

DILUTIONS

BLANKS

NOTE







accredited.










The calculation of Pyrite content assumes that all oxidisable sulphides present in the sample are pyrite. This may not be the case. The calculation

may be an overesitimate when other sulphides such as Barite (Barium Sulphate) are present.


blanks.

























17/8629

WATERS



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:43

JE Job No.:

#

SA

B

DR

M

NA

NAD

ND

NDP

SS

SV

W

+

++

*

AD

CO

LOD/LOR

ME

NFD

BS

LB

N

TB

OC

Matrix Effect

Blank Sample

Client Sample








Not applicable


Dilution required.



No Fibres Detected




Trip Blank Sample

AQC Sample



MCERTS accredited.


17/8629




For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:44

JE Job No: 17/8629


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis


by GC-MS. PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex.


by GC-MS. PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex. Yes


Hydrocarbons (EPH) with carbon banding within the range C8-C40 GC-FID. PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex. Yes

TM5/TM36







PM30/PM12 CWG GC-FID Yes




headspace analysis.




headspace analysis. Yes


(SVOCs) by GC-MS. PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex.


(SVOCs) by GC-MS. PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex. Yes


Chromatography and Electro-Chemical Detection.PM0 No preparation is required.

TM30

Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7, 6010B and BS EN ISO

11885 2009

PM14Analysis of waters and leachates for metals by ICP OES/ICP MS. Samples are filtered for

dissolved metals and acidified if required.



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:44

JE Job No: 17/8629


Prep Method

No. (if

appropriate)

Description

ISO

17025

(UKAS/S

ANAS)

MCERTS

(UK soils

only)

Analysis done

on As Received

(AR) or Dried

(AD)

Reported on

dry weight

basis

TM30

Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -

Optical Emission Spectrometry). Modified US EPA Method 200.7, 6010B and BS EN ISO

11885 2009

PM14Analysis of waters and leachates for metals by ICP OES/ICP MS. Samples are filtered for

dissolved metals and acidified if required.Yes




headspace analysis.Yes


Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM0 No preparation is required.


Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM0 No preparation is required. Yes

TM42 Modified US EPA method 8270. Pesticides and herbicdes by GC-MS PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex.

TM57Modified US EPA Method 410.4. Chemical Oxygen Demand is determined by hot

digestion with Potassium Dichromate and measured spectrophotometerically.PM0 No preparation is required. Yes

TM106 Determination of Sulphide by Skalar Continuous Flow Analyser PM0 No preparation is required.

TM149Determination of Pesticides by Large Volume Injection on GC Triple Quad MS, based

upon USEPA method 8270PM30 Water samples are extracted with solvent using a magnetic stirrer to create a vortex.

NONE No Method Code NONE No Method Code

Subcontracted Subcontracted analysis, sent to an ISO 17025 accredited laboratory where possible.



For

insp

ectio

n pur

pose

s only

.

Conse

nt of

copy

right

owne

r req

uired

for a

ny ot

her u

se.

EPA Export 28-05-2019:04:59:44

Documents

Soils and Groundwater Baseline Screening Assessment & Baseline Report ESB … · 2019. 5. 28. · 13. ESB Site Drainage Testing Completion Report 2017 Project at ESB West Offaly Power,