Air Liquide Australia Ltd Caroline Carbon Dioxide Purification...

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A A i i r r L L i i q q u u i i d d e e A A u u s s t t r r a a l l i i a a L L t t d d C C a a r r o o l l i i n n e e C C a a r r b b o o n n D D i i o o x x i i d d e e P P u u r r i i f f i i c c a a t t i i o o n n P P l l a a n n t t Environmental Impact Report June 2001

Transcript of Air Liquide Australia Ltd Caroline Carbon Dioxide Purification...

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Environmental Impact Report

June 2001

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Caroline Carbon Dioxide Purification Plant Air Liquide Australia LtdEnvironmental Impact Report

Prepared for:

Plant ManagerAir Liquide Australia LtdPO Box 698MOUNT GAMBIERSouth Australia 5290

Prepared by:

Ecos Consulting (Aust) Pty LtdABN 57 081 918 19426 Greenhill RoadWAYVILLESouth Australia 5034

ph: (03) 8357 0400fax: (08) 8357 [email protected]

© Air Liquide Australia Ltd

This publication is copyright. Apart from any fair dealing for private study research, criticism or review, aspermitted under the Copyright Act 1968, no part of this publication may be reproduced, stored in a retrieval systemor transmitted in any form or by any means, electronic, photocopying or otherwise, without prior permission of thecopyright owner.

DOCUMENT CONTROL SHEETDOCUMENT CONTROL SHEET

Caroline Carbon Dioxide Purification Plant - Environmental Impact ReportCaroline Carbon Dioxide Purification Plant - Environmental Impact Report

DocumentReference

RevisionNumber

RevisionDate

Compiledby

Checked by Approved by Comment

ala004rmw A 16/11/00 SC/MCW WEM MCW Issued for comment

ala004rmw B 22/12/00 SC/MCW SC MCW Issued to Air Liquide

ala004rmw 0 15/06/01 SC AB AB Issued to Air Liquide

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Contents

Executive SummaryExecutive Summary .............................................................................................................................................................................. ii

11 IntroIntroductionduction .............................................................................................................................................................................. 11

22 Air Liquide OperationsAir Liquide Operations .................................................................................................................................................. 22

2.1 Location and Access ......................................................................2

2.2 Land Tenure...................................................................................2

2.3 Plant ..............................................................................................22.3.1 Carbon Dioxide Purification Process...............................22.3.2 Carbon Dioxide Vaporisation..........................................42.3.3 Main Purification Train ....................................................42.3.4 Moisture Removal ...........................................................42.3.5 CO2 Liquefaction ............................................................42.3.6 Distillation and Storage...................................................5

2.4 Storage..........................................................................................5

2.5 Loading and Transport ..................................................................5

2.6 Waste Management.......................................................................52.6.1 Disused Solid Waste Pits.................................................52.6.2 General Waste ................................................................52.6.3 Sewage ...........................................................................62.6.4 Chemical Wastes.............................................................62.6.5 Gaseous Emissions..........................................................6

2.7 Water Management.......................................................................62.7.1 Stormwater .....................................................................62.7.2 Produced Formation Water ............................................6

2.8 Well Operations.............................................................................72.8.1 Well History ....................................................................72.8.2 Producing Formations.....................................................72.8.3 Well Completion and Production ....................................7

33 Existing EnvironmentExisting Environment .................................................................................................................................................. 1111

3.1 Land Use......................................................................................11

3.2 Landform and Soils ......................................................................11

3.3 Groundwater ...............................................................................11

3.4 Flora and Fauna...........................................................................11

3.5 Cultural Heritage .........................................................................12

3.6 Downhole Geology and Hydrology..............................................12

3.7 Casing Corrosion/Detection System............................................12

44 Environmental Hazards, Potential Consequences and Management StrategiesEnvironmental Hazards, Potential Consequences and Management Strategies ................ 1313

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55 Environmental ImprovementEnvironmental Improvement................................................................................................................................ 2222

66 ReferencesReferences .............................................................................................................................................................................. 2323

77 AbbreviationsAbbreviations ...................................................................................................................................................................... 2323

AppendicesAppendices

Appendix 1...............................................................Environmental Policy

Appendix 2..................Emergency Response Procedures Caroline-1 Well

Appendix 3...................................................................................... Plates

List of Tables

Table 1: Carbon Dioxide Purification Process Waste Products. .................................. 4Table 2: Casing Dimensions. ...................................................................................... 7Table 3: Potential Environmental Hazards. ............................................................... 13

List of Figures

Figure 1: Plant Location.............................................................................................. 3Figure 2: Stratigraphic Table of the Otway Basin. ...................................................... 8Figure 3: Down Hole Well Assembly .......................................................................... 9

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Executive Summary

Air Liquide Australia Ltd own and operate a carbon dioxide (CO2)purification plant situated near Mt Gambier in the south east of SouthAustralia. The plant produces approximately 21,000 tonnes of CO2

per year and supplies liquid CO2 to clients in South Australia andVictoria.

This Environmental Impact Report has been developed in accordancewith the specific requirements of Part 12 of the South AustralianPetroleum Act 2000 and Regulations 10, 12 and 30 of the PetroleumRegulations 2000.

Potential environmental impacts that may result from the day-to-dayoperation of the plant are predominantly associated with the storage,handling and disposal of hazardous and liquid wastes generated bythe plant and the risk of chemical, fuel or oil spills to land.

Air Liquide have developed a comprehensive set of system and siteprocedures to mitigate potential impacts. Implementation of theseprocedures is conducted in accordance with an ISO 9002 accreditedQuality Assurance System.

As part of Air Liquide's aim to work toward best practice environmentalmanagement, a list of key environmental improvement initiatives tominimise the generation of wastes are also detailed within. Theseinclude the phasing out of silica gel and freon gas and the reduction ofCO2 emissions by 5% by December 2001.

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1 Introduction

Air Liquide Australia Ltd own and operate the Caroline Carbon Dioxide PurificationPlant near Mt Gambier in the south east of South Australia. Construction andoperation of the plant was approved under the South Australian Petroleum Act1940 and the plant was commissioned in 1967. This Act has recently beenrepealed and replaced with the South Australian Petroleum Act 2000. Under thecurrent Act operators must comply with a range of new requirements, particularlywith regard to environmental management.

As a requirement of Part 12 of the Petroleum Act 2000, a regulated activity canonly be conducted if an approved Statement of Environmental Objectives (SEO)has been developed. The SEO outlines the environmental objectives that theregulated activity is required to achieve and the criteria upon which the objectivesare to be assessed. The SEO is developed on the basis of the informationprovided in an Environmental Impact Report (EIR). An EIR is provided by thelicensee and describes an activity’s likely impacts on the environment andmanagement strategies to minimise these impacts.

Ecos Consulting (Aust) Pty Ltd has been commissioned by Air Liquide to preparean EIR and SEO for the Carbon Dioxide Purification Plant. Preparation of bothdocuments was based upon:

§ site inspection and review of plant operations on October 18 2000;§ review of Air Liquide’s existing environmental documentation (policies,

procedures, incident reports, monitoring results, induction and trainingprocedures, and audit reports);

§ interviews with the Plant Manager;§ liaison with the Department of Primary Industries and Resources South

Australia (PIRSA) to ensure that specific requirements of the EIR were fullyunderstood; and

§ through Air Liquide, consultation with, or correspondence from, theEnvironment Protection Authority, District Council of Grant, Department ofEnvironment and Heritage, Forestry South Australia and Carter Holt Harvey.

This EIR addresses potential environmental impacts associated with the day-to-dayoperation of the plant and outlines strategies and procedural requirements for theappropriate management and mitigation of these impacts.

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2 Air Liquide Operations

2.1 Location and Access

The Carbon Dioxide Purification Plant is located on Carba Road, approximately 12kilometres southeast of Mt. Gambier, and occupies an area of almost 2 hectares(Figure 1). All access to the site is via Carba Road, which is an all-weather publicroad maintained by the District Council of Grant.

2.2 Land Tenure

The Plant is situated within Petroleum Production Licence 21, which overlies theCaroline Forest Reserve, managed by Forestry SA.

2.3 Plant

2.3.1 Carbon Dioxide Purification Process

Carbon dioxide (CO2) was initially discovered at the plant site by Alliance OilDevelopment Australia in 1967. Construction of the wellhead and the associatedpurification plant was completed in 1967 and CO2 production commencedimmediately.

Currently, raw CO2 is supplied to the Air Liquide plant from the well via a 70 metreflowline. The plant runs continuously and at the present time producesapproximately 21,000 tonnes of CO2 per year. The plant supplies liquid CO2 to thesoft drink, firefighting, medical and winemaking industries in South Australia andVictoria.

Raw liquid from the well contains approximately 90 – 94.5% CO2, and 6.5 -10%impurities. These impurities include sulphur compounds (mainly H2S), nitrogen anda number of light and heavy hydrocarbons. In addition, some free water is alsocontained within the raw liquid. A purification process is required to remove theseimpurities and produce CO2 to a standard that meets consumer specifications.

A summary of waste generated as a result of the CO2 purification process is givenin Table 1.

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Figure Figure 11: Plant Location.: Plant Location.Source: S.A. Department of Lands, Gambier Topographic Map

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Table Table 11: Carbon Dioxide Purification Process Waste Products.: Carbon Dioxide Purification Process Waste Products.

ProcessProcess Type of WasteType of Waste Quantity Generated (annually)Quantity Generated (annually)

CO2 Vaporisation Solid hydrocarbonWater

10, 000 l9,000 l

Main Purification Train PuraspecActivated carbonWater vapour

5,000 kg2,500 kgundetermined

Moisture Removal Silica gelWater vapour

800 kgundetermined

CO2 Liquefaction No waste generated N/A

Distillation and Storage CO2

Methane

Nitrogen

25% total production (on average)1-1.5% volume of vented CO2 (quantityas above)undetermined

2.3.2 Carbon Dioxide Vaporisation

Initially raw CO2 liquid is heated and CO2 is vaporised. Water, that is used in theheating process, is sourced from a licenced bore located on site. Heating water isdosed with corrosion inhibitor and sulphuric acid to prevent corrosion, controlcalcium build-up and maintain the pH of the water. Carbon dioxide vapour exitsthe vaporiser leaving behind some hydrocarbon and waste water. Wastehydrocarbon and water is stored in a bunded tank (Plate 1). Waste water is laterremoved from this tank and pumped to the “effluent” storage tank.

2.3.3 Main Purification Train

The bulk of sulphur impurities are removed from the CO2 stream at this stage ofthe purification process. Both Puraspec media and activated carbon are used toabsorb sulphur components. The adsorption process also removes odours fromthe CO2 vapour and some hydrocarbons. During the purification process Puraspecis converted to copper sulphide and cannot be regenerated. Activated carbon isregenerated and used for a period of twelve months before it is replaced with newmaterial.

2.3.4 Moisture Removal

From the main purification train CO2 vapour flows to two absorption driers. Thedriers contain silica gel, which removes almost all moisture from the CO2 vapour.Silica gel is regenerated for four to six months before being removed andreplaced.

2.3.5 CO2 Liquefaction

Once dried, the CO2 flows through a dust filter before being liquefied. The drystream is liquefied via refrigeration. At this stage the only significant contaminantsstill present in the CO2 are nitrogen and methane.

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2.3.6 Distillation and Storage

Low pressure CO2 liquid is distilled then stored in vessels where it is held atapproximately 1,750-1,800 kPa. During the distillation process aCO2/methane/nitrogen mixture vents to the atmosphere (methane makes upapprox. 1 – 1.5% of 3,000kg CO2 vented per hour).

2.4 Storage

The only flammable liquids stored on site are diesel (180 l), unleaded petrol (300 l),and a small quantity of paint. Unleaded petrol and paint are stored undercover ina workshop storage area (Plate 2). The diesel is contained near the wellhead andacts as a “tell-tale” gas leak indicator (Plate 3).

Some biocide (40 l) is kept in the workshop storage area.

Sulphuric acid (200 l), anhydrous ammonia (240 kg), and corrosion inhibitor (40 l)are stored alongside the number one cooling tower.

Small quantities of lubrication and refrigerant oil are also stored on site (total ofapprox. 100 l).

Aside from some pure CO2 storage (in addition to processed CO2), the only othergases stored on site are cylindered oxygen and acetylene gases and a smallquantity of freon. Freon is kept for refrigeration purposes.

2.5 Loading and Transport

On average, between three and five road tankers per day load liquid CO2 on-site(Plate 4) and transport it to clients within South Australia and Victoria.

2.6 Waste Management

2.6.1 Disused Solid Waste Pits

Two disused solid waste pits within an area of 4 x 5 m wide and 1 m deep werebackfilled in 1984. All wastes are now currently disposed of off-site by a licencedcontractor.

2.6.2 General Waste

All general wastes (including solid wastes, paper and domestic scraps) arecollected in a hopper for later removal to a licenced disposal facility.

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2.6.3 Sewage

All sewage is stored in a concrete effluent pit near the western boundary of thesite. A licenced waste disposal contractor pumps out the pits periodically andtransports the waste to a licenced sewage treatment plant.

2.6.4 Chemical Wastes

Chemical wastes including spent silica gel, activated carbon and Puraspec arecollected by a licenced waste disposal contractor for disposal off-site.

Empty chemical drums are returned to the bunded workshop storage area forsubsequent collection and disposal off-site.

2.6.5 Gaseous Emissions

Venting of CO2 vapour (including fugitive releases) and methane is required duringoperations. Air Liquide is currently aiming to reduce CO2 losses from 25% to 20%by 2001. This will also reduce methane emissions.

2.7 Water Management

2.7.1 Stormwater

All rainwater runoff within the immediate vicinity of the plant is collected inconcrete drainage channels and temporarily stored in a settling pit before beingpumped to the “effluent” storage tank (Plate 5). Produced formation water is alsostored in the storage tank. After a settling period all water from the “effluent”tank is pumped to an adjacent tank and aerated before being disposed of viairrigation of grassed areas within the plant site. Irrigation takes place via a singlesprinkler that is moved throughout the site.

There are no natural drainage lines located either within the site or in theimmediate surrounding environment.

2.7.2 Produced Formation Water

Produced formation water is temporarily stored in a holding tank before beingpumped to the "effluent" storage tank. This water is disposed of along withstormwater for irrigation on-site.

The "effluent" storage tank is cleaned out once a year to remove any build up ofsolids (sediment and hydrocarbons). Hydrocarbons are derived from smallquantities present in the produced formation water and from plant washdown andmaintenance.

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2.8 Well Operations

2.8.1 Well History

The source of the CO2 (and produced formation water) is the Caroline-1 well whichwas spudded by Alliance Oil Development Australia N.L. in September 1966 andreached a total depth of 11, 066ft (3373m) in January 1967. The well wascompleted in February 1967 as a CO2 producer.

The deepest formation penetrated is the Eumeralla Formation of the OtwayGroup.

2.8.2 Producing Formations

After a series of drillstem tests the well was completed in two upper units of theOtway Group (Waarre Formation and a transition unit between the Waarre andEumeralla Formations). Production from the well since February 1968 has shownthat the vast majority of the CO2 comes from two small, perforated intervals in theWaarre Formation (8204-8210 and 8214-8230ft RKB). Figure 2 shows astratigraphic table for the Otway Basin and Figure 3 illustrates the wellbore andthe perforated intervals in the Waarre Formation.

2.8.3 Well Completion and Production

The well was completed as a single completion, producing through a 2 � inchtubing with a packer set in the 5 ½ inch production casing at 8130ft. The openperforations are located at:§ 8204 - 8210 ft (6 ft);§ 8214 - 8230 ft (16ft);§ 9152 - 9172 ft (20ft); and§ 9303 - 9321 ft (18ft).

The plugged-back total depth was 9400ft, but fill has reduced this to 9322ft by2001.

Casing was run and cemented with sizes, weights and depths as outlined in Table2.

Table Table 22: Casing Dimensions.: Casing Dimensions.

Size (inches)Size (inches) Weight (lbs)Weight (lbs) Depth (ft)Depth (ft)

19½ NA 163

13� 48 740

9� 36 3149

5½ 17 9400 (J-55 and N-80)

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Figure Figure 22: Stratigraphic Table of the Otway Basin.: Stratigraphic Table of the Otway Basin.

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Figure Figure 33: Down Hole Well Assembly: Down Hole Well Assembly

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Apart from intermittent production during 1968, the well has produced CO2 almostcontinuously at an average rate of 1.25 million SCFPD (65 tonnes per day). Themaximum continuous rate is approximately 1.9 million SCFPD (100 tonnes per day).

No workover has been performed on the well.

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3 Existing Environment

3.1 Land Use

The plant is situated within the Caroline Forest Reserve and surrounding land useconsists solely of pine plantations for timber production. The nearest alternatelanduse is grazing, some 4.5km to the south. The closest residence is over 5kmfrom the Plant.

The forests in the Caroline region are primarily for wood production and havelimited opportunities for recreation. Public access along Carba Road is permitted.

3.2 Landform and Soils

The plant site is relatively flat. The surrounding Caroline Forest area is generallylow lying and gently undulating, with elevations ranging from 25 to 85 metresabove sea level (Geddes 1981). There are no natural drainage lines (i.e. surfacestreams and rivers) in the area.

A calcarenite range (weathered dune) runs through the Caroline Forest region,hence soils in the area consist mainly of deep sands (Geddes 1981; Croft et al.1999).

3.3 Groundwater

The groundwater level occurs at a depth of approximately 22m. The Departmentfor Water Resources routinely samples groundwater (every 3 months) from thebore on the eastern perimeter of the plant site. Samples are analysed for a rangeof parameters (including major anions and cations, conductivity, salinity and pH.).Samples are taken for a Department of Water Resources monitoring programwhich aims to assess the level and quality of groundwater at various bores in thesouth east.

3.4 Flora and Fauna

The plant site consists of maintained grassed areas with some scattered treesalong the perimeter. Some of these are native to the area (eg Eucalyptus obliqua),while others appear to have been planted since the establishment of the plant (egE. globulus). The site is surrounded by Pinus radiata plantations, with the nearestarea of native vegetation being approximately 1.5 km to the east (Native ForestReserve). The only potential source of weeds is via the movement of vehicles toand from the plant site. This risk is not considered significant as all vehicles(including tankers) access the site using public roads. Given the context of

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surrounding land-use, the relatively small size of the plant site and absence ofnative vegetation in the area the consequences of any weed introduction are notconsidered significant. Little natural fauna habitat exists in the surrounding area.

3.5 Cultural Heritage

No items of indigenous or non-indigenous cultural heritage are present on the site.

3.6 Downhole Geology and Hydrology

The Gambier Formation of the Glenelg Group is the major ground water source inthe region. This formation extends down to a depth of 640ft RKB (Figure 2).Below this depth only brackish (non-potable) water has been encountered.

3.7 Casing Corrosion/Detection System

The annulus between the 5½ inch casing and the 2� inch production tubing (abovethe packer) is almost completely filled (to the surface) with mud which was used todrill the well. The remaining space is filled with diesel oil, which is allowed to draininto the annulus as it expands or be expelled out of the annulus as it contracts dueto temperature fluctuations.

The purposes of this system are:

§ To ensure that air does not enter the casing/tubing annulus, thus providingcorrosion protection; and

§ To provide a surface indication of downhole problems such as ruptures in thetubing or casing by means of a check valve and pressure gauge.

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4 Environmental Hazards,Potential Consequences andManagement Strategies

The well and its wellhead pose a number of threats to the environment and publicsafety. These include, downhole blowout, well casing/tubing corrosion, wellheadrupture and chemical, fuel or oil spill. Potential environmental hazards resultingfrom the Carbon Dioxide Purification Plant operations are summarised in Table 3.

Table Table 33: Potential Environmental Hazards.: Potential Environmental Hazards.

OperationOperation HazardHazard

Plant operation:§ CO2 production§ CO2 purification§ Storage§ Loading and transport

§ Chemical, fuel or oil spill§ Liquid waste storage and disposal§ Solid waste storage and disposal§ Atmospheric emissions§ Wellhead rupture§ Fire or explosion§ Downhole blowout§ Well casing corrosion

Site wash down and run-off § Disposal of contaminated run-off water

Administration § Domestic waste disposal§ Sewage effluent storage and disposal

The proposed environmental objectives and management strategies for theenvironmental hazards and potential consequences of the Carbon DioxidePurification Plant operations are outlined in Table 3. These have been developedto be consistent with Air Liquide’s Environmental Policy (Appendix 1).

Site procedures are implemented in accordance with an ISO 9002 accreditedQuality Assurance System. System procedures include training, recordmanagement, monitoring, auditing and reporting.

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Table 3: Environmental hazards, potential consequences and objectives and management.Table 3: Environmental hazards, potential consequences and objectives and management.

Management StrategiesManagement StrategiesEnvironmental HazardsEnvironmental Hazards Potential ConsequencesPotential Consequences Environmental ObjectivesEnvironmental Objectives

Site ProceduresSite Procedures System ProceduresSystem Procedures

Chemical, fuel or oil spill. Contamination of groundwaterand/or soil.

Comments:

• A spill is any unintendedleakage or escape of achemical, fuel or oil.

• Any chemical, fuel or oilspill at the plant site isexpected to be relativelylow in volume (max. 300l ofunleaded petrol) andlocalised (ie. within thecontained storage area).

• All spills, no matter whatvolume, are to beaddressed.

Avoid groundwater and soilcontamination.

Ensure that chemicals, fuels andoils are stored in a containedarea and on a flat, impermeablesurface.In the event of a spill ensurethat spill response proceduresare followed (refer SafetyTraining Manual – CryogenicLiquids, Spills and VapourClouds or Material Safety DataSheet) and that the incident isreported to the Plant Manager.

Maintain existing spill responsestation.

Bund sulphuric acid storagearea.

Integrate environmentalincident reporting into existingincident reporting systems (i.e.QIR).Provide appropriate trainingand/or induction to employeesand contractors with regard tospill response and reporting.

Establish and maintain a recordof all spills and ensure thatappropriate corrective actionsare carried out.

Ensure that relevant MaterialSafety Data Sheets and spillresponse procedures areposted in appropriate workareas.

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Management StrategiesManagement StrategiesEnvironmental HazardsEnvironmental Hazards Potential ConsequencesPotential Consequences Environmental ObjectivesEnvironmental Objectives

Site ProceduresSite Procedures System ProceduresSystem Procedures

Liquid waste storage anddisposal:§ stormwater§ produced water§ hydrocarbons

Contamination of groundwaterand/or soil with hydrocarbons.

Comments:

• Discharge of stormwaterand formation water viairrigation may result insaturation of the soil profileand/or build-up ofhydrocarbons and salt.

• The pH of the soil may alsobe affected (ie. decrease)by prolonged irrigationwith formation water.

Minimise waste generation.Avoid groundwater and soilcontamination.

Avoid creation of soakages byensuring that the sprinkler isrelocated before soil becomessaturated and pools of waterdevelop.

Inspect condition of grassedareas for signs of “die-off” orsurface hydrocarbons.Minimise hydrocarbon contentof discharge (irrigation) waterby ensuring adequate retentiontime in hydrocarbon storagetank and “effluent” storagetank.Check effluent tank andbunded area to ensure thatspills or leaks are not occurring.Any build up of hydrocarbonsto be regularly removed bylicenced contractor.

Off-site disposal ofhydrocarbons to be conductedby licenced contractor.

Maintain contract with licencedwaste removal contractor.

Sample and analyse liquidwaste 6-monthly. Check resultsagainst ANZECC water qualityguidelines for agriculture (testfor 30mg/l or below forhydrocarbons).Develop a checklist forinspection of grassed areas,“effluent” tanks, hydrocarbonstorage tank and bunds.

Maintain a record of inspectionsand water quality monitoringdata.

Address any issues identifiedduring inspections ormonitoring.

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Management StrategiesManagement StrategiesEnvironmental HazardsEnvironmental Hazards Potential ConsequencesPotential Consequences Environmental ObjectivesEnvironmental Objectives

Site ProceduresSite Procedures System ProceduresSystem Procedures

Solid waste storage anddisposal

Contamination of groundwaterand/or soil.

Comments:

• The following solid wastesare generated on-site:

Puraspec

activated carbon

silica gel

domestic wastes

• All waste is stored in asealed area (approx. 6 ×4m) and collected anddisposed of by a licensedwaste removal contractor.Hence, the risk ofcontamination to the soilsor groundwater isconsidered low.

Minimise waste generation.Avoid groundwater and soilcontamination.

Contain and handle waste incontainers and, whereappropriate, within bundedareas.

Maintain contracts withlicenced waste removalcontractors.

Phase-out use of silica gel andreplace with Trockenperlen N(March 2001).

Check and control wasteremoval contracts.

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Management StrategiesManagement StrategiesEnvironmental HazardsEnvironmental Hazards Potential ConsequencesPotential Consequences Environmental ObjectivesEnvironmental Objectives

Site ProceduresSite Procedures System ProceduresSystem Procedures

Solid waste storage (historical) Contamination of soil and/orgroundwater.

Comments:§ The following solid wastes

were contained within thedisused waste pits:§ Puraspec§ activated carbon§ silica gel

§ There is the potential forlocalised (pits are 4 * 5mwide and 1m deep)contamination of the soiland/or groundwater byhydrocarbons and/orcopper sulphate

Avoid groundwater and soilcontamination.

Undertake soil and sampling(for petroleum hydrocarbons) inthe vicinity of the disused wastepits (first quarter 2001).

On the basis of the results ofsoil sampling, decide on theneed for groundwater testing,and initiate if warranted.Carry out any necessaryremediation of waste pits andthe surrounding environment.

Ensure sampling andmonitoring results are checkedand recorded and that anynecessary actions areimplemented.

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Atmospheric emissions:§ CO2 venting§ fugitive emissions (CO2)§ methane§ disposal of “off-spec” CO2

gas

Atmospheric pollution(greenhouse gas).

Danger to health and safety ofpersonnel, contractors and thepublic.

Comments:§ The only risks associated

with release of off-specification gas arise fromdirect contact with CO2vapour (ie. suffocation andfrostbite).

§ Plant emissions are off-set(to some extent) by localCO2 absorption by thesurrounding pineplantation.

§ Past emissions of “off-spec” gas have occurredinfrequently (eg. onceevery eight to ten years).

Minimise Air Liquide’scontribution to the“greenhouse effect”.

Ensure that plant design andoperational standards minimisefugitive emissions (as per GasOperations Manual V.1&2 andSite Operation Manual).

Ensure that plant operatingprocedures result in efficientplant operation (refer SiteOperation Manual).

Ensure that plant operatingprocedures result in specifiedgas quality.

Operate plant in accordancewith existing specifiedprocedures (refer SiteOperation Manual).Monitor with gaschromatograph to providemore immediate analysis ofproduct quality.

Dispose of “off-spec” CO2 gasaway from the immediatevicinity of operations, personneland the public (ie downwindand 30m from nearest roadand/or personnel).

Conduct a regular maintenanceprogram to reduce fugitiveemissions (refer Site OperationManual).

Inspect and monitormaintenance works.

Keep a record of maintenanceworks and ensure that worksprogress as scheduled.

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Management StrategiesManagement StrategiesEnvironmental HazardsEnvironmental Hazards Potential ConsequencesPotential Consequences Environmental ObjectivesEnvironmental Objectives

Site ProceduresSite Procedures System ProceduresSystem Procedures

Atmospheric emissions:§ freon.

Atmospheric pollution (ozonedepleting substance).

Minimise Air Liquide’scontribution to ozonedepletion.

Store and handle freonappropriately.

Ensure that Freon is removedfrom site and disposed of by anaccredited contractor

Phase-out use of freon gas forrefrigeration and replace withR22 (2-5% ozone depletioncapability of freon) by end June2002.

Well casing corrosion Contamination of soil and/orgroundwater.

Comments:

• Currently wellheadpressure and a “tell-tale”diesel system indicate ifthere is any lose ofpressure, and thereforepotential leakage due tocorrosion, in the well.

Avoid groundwater and soilcontamination.

Continue to monitor wellheadpressure and “tell tale” dieselsystem daily (refer DailyOperations Manual).

Continue well surveys (surveyscarried out by Questaapproximately every two years).

Maintain a record of dailyinspections and monitoringdata (refer Daily OperationsManual).

Ensure well survey reports arechecked and filed and that anynecessary works are carriedout.

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Management StrategiesManagement StrategiesEnvironmental HazardsEnvironmental Hazards Potential ConsequencesPotential Consequences Environmental ObjectivesEnvironmental Objectives

Site ProceduresSite Procedures System ProceduresSystem Procedures

Wellhead rupture (refer toAppendix 2: EmergencyResponse Procedures -Situations)

Danger to health and safety ofemployees, contractors andpossibly the public.

Comments:

• The risk of a wellheadrupture is considered to below (as per Risk/ResultDiagram – EmergencyResponse ProceduresCaroline-1 Well (Appendix2))

Provide a safe workingenvironment for employees,contractors and third parties.

Continue to monitor pressureand temperature at thewellhead and the condition ofwell tubing every two years(well surveys carried out byQuesta).

Continue to monitor wellheadpressure and temperature daily(refer Daily Operations Manual).

Record daily measurements ofwellhead pressure andtemperature (refer Daily LogSheets and Daily OperationsManual).

Maintain Emergency ResponseProcedures (refer EmergencyResponse Procedures Caroline-1 Well and Training SafetyManual) and update asrequired.

Ensure that all personnel andcontractors are aware ofrelevant emergency responseprocedures.

Ensure that emergencyresponse procedures areposted in appropriate workareas.

Maintain a record of wellheadsurvey reports.

Downhole blowout Loss of production of CO2

and/or contamination of soiland groundwater.

Comments:

• All data obtained from wellsurveys indicate that this ishighly unlikely to occur.

Maintain well tubing inadequate condition to resistrupture.

Continue to monitor wellheadpressure and “tell tale” dieselsystem daily (refer DailyOperations Manual).

Continue well surveys (surveyscarried out by Questaapproximately every two years).

Maintain a record of dailyinspections and monitoringdata (refer Daily OperationsManual).

Ensure well survey reports arechecked and filed and that anynecessary works are carriedout.

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Management StrategiesManagement StrategiesEnvironmental HazardsEnvironmental Hazards Potential ConsequencesPotential Consequences Environmental ObjectivesEnvironmental Objectives

Site ProceduresSite Procedures System ProceduresSystem Procedures

Fire or explosion Danger to health and safety ofemployees, contractors andpossibly the public.

Comments:

Risk of fire or explosion isconsidered low as:

• CO2 is not flammable;

• Hydrocarbons are presentat levels below flammablelimit; and

• Other flammable materials(eg diesel and unleadedfuel) are present in smallquantities.

Provide a safe workingenvironment for employees,contractors and third parties.

Operate plant in accordancewith approved procedures toprevent over-pressure (referDaily Operations Manual andGas Operations Manual).

Maintain fire-fightingequipment on-site.

Ensure that all personnel andcontractors are aware ofrelevant emergency responseprocedures (refer EmergencyResponse Procedures Caroline-1 Well).

Ensure that emergencyresponse procedures areposted in appropriate workareas.

Storage and disposal of sewageeffluent.

Contamination of groundwaterand/or soil.

Avoid groundwater and soilcontamination.

Maintain contract with licencedwaste removal operator.

Inspect trench area weekly forobvious leaks.

Check and control contracts.

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5 Environmental Improvement

Air Liquide aims to work toward best practice environmental management for theCaroline Carbon Dioxide Purification Plant operation. To meet this commitment,Air Liquide will:

§ promote environmental awareness among all personnel on site, includingcontractors, through appropriate training and inductions;

§ develop environmental incident reporting procedures and integrate intoexisting ISO 9002 Quality Assurance System;

§ comply with all requirements of PPL21;

§ reduce CO2 losses by 5% over the next twelve months;

§ phase-out the use of freon gas and replace with R22 within the next 18months;

§ reduce solid waste generation by phasing-out the use of silica gel andreplacing with Trockenperlen N within the next six months;

§ undertake sampling of soil at the disused waste pits during the first quarter2001;

§ monitor the quality of water disposed of on-site via irrigation.

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6 References

The following documents were reviewed as part of the preparation of the EIR:

Geddes, D.J. (1981). Plantation re-establishment following the CarolineForest fire: an interim review. Woods and Forests Department of SouthAustralia, Miscellaneous Publication No.2.

Croft, T., Carruthers, S., Possingham, H., and Inns, B. (1999). BiodiversityPlan for the south east of South Australia. Department for Environment,Heritage and Aboriginal Affairs.

7 Abbreviations

Air Liquide Air Liquide Australia Limited

ºC Degrees Celsius

CO2 Carbon dioxide

Ecos Ecos Consulting (Aust) Pty Ltd

EIR Environmental Impact Report

H2S Hydrogen Sulphide

kg Kilogram

kPa Kilo Pascals

l Litre

m Metre

mm Millimetre

PIRSA Primary Industries and Resources, South Australia

PPL Petroleum Production Licence

ppm Parts per million

SCFPD Standard Cubic Feet Per Day

SEO Statement of Environmental Objectives

SO2 Sulphur dioxide

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Appendix 1

Environmental Policy

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Appendix 2

Emergency ResponseProcedures Caroline-1 Well

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Appendix 3

Plates

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Plate 1: Bunded hydrocarbon storage tank (centre) and “effluent”storage tank (immediate foreground).

Plate 2: Contained storage area.

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Plate 3: Well head (left) and “tell-tale” diesel system (right).

Plate 4: CO2 transport tanker in loading area.

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Plate 5: “Effluent” storage tank.