Item 02. Environmental Management Plan for RAAF Base

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Contents

Introduction .......................................................................................... 1 PART A – Environment and Heritage Strategy ..................................31. Introduction ....................................................................................3

1.1 Background.......................................................................................31.2 Site Location and Activities ...............................................................31.3 Defence Environmental Policy ..........................................................41.4 Role of the Environment and Heritage Strategy ...............................4

2. Facility Description ........................................................................52.1 Location ............................................................................................52.2 Site History........................................................................................52.3 Defence Activity ................................................................................52.4 Environmental Values .......................................................................6

3. Environmental Management Program ..........................................73.1 Legislation and Policy Obligations ....................................................7

3.1.1 Commonwealth Legislation..............................................................73.1.2 Territory Legislation .........................................................................73.1.3 Defence Instructions and Policies....................................................7

3.2 Responsibilities for Current Environmental Management.................83.3 Monitoring and Reporting..................................................................93.4 Audit Requirements ........................................................................103.5 Awareness and Training Requirements..........................................11

4. Environmental Objectives ...........................................................134.1 Introduction .....................................................................................13

4.1.1 Environmental Management System .............................................134.1.2 Sustainable Use of the Base..........................................................134.1.3 Pollution and Contamination Prevention and Management ..........134.1.4 Natural Resource Conservation.....................................................134.1.5 Heritage Management ...................................................................134.1.6 Relationship with the Community...................................................14

5. Strategic Action Plans ................................................................. 155.1 Fire Management............................................................................165.2 Waste Management........................................................................185.3 Noxious and Environmental Weeds and

Feral Animals Management .........................................................215.4 Hazardous Materials Management .................................................245.5 Water Management ........................................................................275.6 Soil Management ............................................................................305.7 Cultural Heritage .............................................................................325.8 Social and Community Issues.........................................................345.9 Fuel Management ...........................................................................365.10 Mosquito Control.............................................................................385.11 Flora and Fauna and Habitat Management ....................................40

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PART B – Implementation Plan .........................................................43Table 1 Fire Management .......................................................................44Table 2 Waste Management ...................................................................46Table 3 Noxious and Environmental Weeds and

Feral Animals Management.....................................................49Table 4 Hazardous Materials Management.............................................53Table 5 Water Management ....................................................................55Table 6 Soil Management........................................................................57Table 7 Cultural Heritage.........................................................................59Table 8 Social and Community Issues .....................................................61Table 9 Fuel Management.......................................................................62Table 10 Mosquito Control ......................................................................64Table 11 Flora and Fauna and Habitat Management...............................65

Appendix A Environmental Legislation .......................................67

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Document History and StatusIssue Rev. Issued To Qty Date Reviewed ApprovedDraft 1 DEO-NT 1 2 May 2001 B Brown B Brown

Seconddraft

2 DEO-NT, stakeholders 5 15 May 2001 B Brown B Brown

Final 6 DEO-NT 6 19 July 2001 B Brown B Brown

Printed: 19 July, 2001Last Saved: 21 May, 2018File Name: I:\DARWIN\Dr04650.699\Dr04674\Technical\R02lvrxx.Doc

Project Manager:Name of Organisation: Department of DefenceName of Project: Phase 3Name of Document: Environmental Management Plan

for RAAF Base TindalDocument Version: FinalProject Number: DR04674

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IntroductionThe Department of Defence has commissioned the preparation of an Environment Management Plan (EMP) for the facilities at RAAF Base Tindal (RBT), located south-east of the township of Katherine, NT. This report comprises an Environment and Heritage Strategy (EHS) and Implementation Plan (IP), and whilst the EHS and IP are separate documents, together they form the facility EMP.

The EMP addresses environmental issues at RBT and presents objectives and strategies for managing these issues. The document also includes a structured schedule of management actions detailing responsibilities and timeframes. It is a tool to be used by key stakeholders to plan resources and execute environmental management programs.

As part of the development and master planning for RBT in the early 1980s, a number of environmental studies and consultations were undertaken. The information obtained formed the basis of an Environmental Impact Statement (EIS) which described potential environmental effects of the proposed development. The EIS also detailed mitigation measures for these effects and these commitments were assembled into an Environmental Management Plan (EMP) for RBT. The EMP was compiled by Kinhill Engineers Ptd Ltd and released in October 1987.

In August 2000, Sinclair Knight Merz completed an Initial Environmental Review (IER) of the Base which was the first phase in the process to formulate a more current EMP relevant to present and foreseeable activities undertaken at RBT. The IER identified aspects of RBT’s operations which have an actual or potential impact on the on-site or off-site environment. Due to extensive information compiled during EIS and 1987 EMP development, the IER did not identify any significant shortfalls in information, and hence the second phase of EMP development, an Environmental Impact Assessment (EIA), was not deemed necessary. As such, in February 2001, Sinclair Knight Merz was engaged to undertake the third phase of EMP development, that being the formulation of an EHS and IP.

Having identified the environmental aspects, an EHS/IP has been prepared to form an EMP. This Plan addresses these aspects and present objectives, strategies and procedures to implement these strategies to ensure adequate environmental management of RBT. The document is an upgrade of the 1987 EMP and effectively replaces the EMP. This document should therefore be used as guidance for environmental management issues at RBT.

This document has been split into two sections:Section A – represents the EHS; andSection B – details the IP.

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PART A – Environment and Heritage Strategy

1. Introduction1.1 BackgroundThe purpose of the Environment and Heritage Strategy (EHS) is to provide a workable and relevant management process for RAAF Base Tindal that effectively manages its environmental and heritage values. This EHS was developed from information primarily sourced from the Phase 1 Initial Environmental Review (IER) (SKM, August 2000), consultation with RAAF Tindal and Corporate Services & Infrastructure Centre – Northern Territory/Kimberley (CSIC-NT/K) – Infrastructure Division (ID) and Service Delivery Division (SDD).

Environmental issues which have been identified as a high priority and which have been addressed in the EHS include:

fire management;contamination of stormwater and groundwater from wastewater discharges andoperation of on-site sewer systems;fuel management; andwaste management;

1.2 Site Location and ActivitiesRAAF Base Tindal (RBT) is located approximately 320 km south-east of Darwin and approximately 13 km south-east of the township of Katherine, NT. The site covers an area of about 122 km2 of which approximately 5 km2 comprises paving, runways and buildings. The site location is shown in Figure 1 – Site Location Map.

RBT is a joint civil-military airfield which was originally developed as a ‘bare base’ between 1963-1970 and which underwent significant upgrading and expansion in the 1980s. The primary role of RBT is to provide a home for 75 Squadron which forms part of the Air Force’s Tactical Fighter Force.

There are a number of activities undertaken at RBT including:ordnance preparation and storage;refuelling of vehicles and aircraft;aircraft maintenance, washing and painting;fuel testing;light engineering works (vehicle maintenance, welding, aircraft engine works);security, including police dog training;radar communications;medical facilities;catering;photography of aircraft and personnel;fire fighting services;accommodation;ground defence training;search and rescue (SAR) undertaken by contractors Lloyds;


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lease of land to Frontline who run a canteen and service station for private use byBase personnel and the public;lease of land to Katherine City Council who manage the Katherine Airport; andair movements of military passengers and cargo.

The current layout of RBT is shown in Figure 2 – RAAF Base Tindal Layout Plan.This plan shows all the areas at which the above activities take place, including theliving quarters and recreational facilities.

The Hill Radar 202 Facility is located approximately 4 km east of RAAF Base Tindal, on the Stuart Highway. The main activities undertaken at the radar facility are general maintenance of radar and communications equipment, monitoring of radar and air to ground communications.

1.3 Defence Environmental PolicyAs a Department of Defence establishment, RBT is subject to the Defence Environment Policy Statement, 1998. The Policy details environmental goals and principles that the Department of Defence has committed to for all of its sites. It reflects the commitment that Defence has to sound environmental management. The Policy promotes pro-active management of the environment by all Defence personnel, stressing the issue of ‘duty of care’. It provides principles which personnel should follow to ensure that environmental protection is incorporated into day to day Defence activities. Further details on the Policy are provided in Section 3.1.3.

1.4 Role of the Environment and Heritage StrategyThe purpose of the EHS in the EMP context is to describe aspects of the environment requiring active management, the best approach to this management and the resources needed to complete the management process. Provision of a workable and relevant management process will effectively protect the environmental values of RBT.

The Environment and Heritage Strategy (EHS) aims to identify site specific environmental management objectives and strategies for managing significant issues relevant to RBT. Performance criteria, monitoring and reporting requirements are also detailed. Issues and strategies have primarily been obtained from the 1987 EMP and the Phase 1 IER (2000). This document will describe the process for achieving effective management of environment and heritage issues and in doing so, the EHS will effectively replace the 1987 EMP. The EHS is directly linked to the IP, and together they are the key documents that will be used by personnel responsible for the management of RBT, to plan resources and activities and execute environmental management programs.


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2. Facility Description2.1 Location RAAF Base Tindal is located 320 km south-east of Darwin and approximately 13 km south east of the township of Katherine, NT.

The total site is bounded by:grazing and rural/residential land to the north (Jarridale Station);rural land and the Cutta Cutta Caves National Park to the south;rural land and mango farms to the east; andgrazing land and a quarry, from which blue metal road base is mined, to the west.

The site location is shown in Figure 1 – Site Location Map.

2.2 Site HistoryTindal was originally known as Carson’s Airfield. Construction at RBT was begun during WWII by an American engineer regiment and it was completed in 1944 by an element of the Victorian Country Roads Board. The small airfield/base, as it was then, was mainly built for exercises and civilian use, and was never used operationally, or had any aircraft squadrons based there during WWII. The base was renamed Tindal after Wing Commander A.R. Tindal who was Commanding Officer of No 24 Squadron based at Darwin in 1941. He was killed in action in 1942 during the first Japanese air raid on Darwin.

Re-construction and extension to RBT was commenced in the late 1950s and early 1960s by the RAAF’s No 5 Airfield Construction Squadron to provide a backup airfield for Darwin. From 1963 to 1970, RBT was further upgraded for use as an airfield for exercises and civilian use and was used as a ‘bare base’. Significant upgrading and expansion in the 1980s resulted in, more or less, the Base as it is today.

In 1987, RAAF Base Tindal was established. RBT is under the control of 322 Combat Support Wing, with its primary role being to provide a home for 75 Squadron, which forms part of the Air Force’s Tactical Fighter Force.

2.3 Defence ActivityActivities undertaken by Defence at RBT were briefly listed in Section 1.1. RBT is the main tactical fighter base in the Northern Territory. 75 Squadron (the fighter squadron) maintains all F/A -18 aircraft at RBT including disassembly, servicing and reassembly of aircraft components, surface finish repairs on aircraft, maintenance of avionics equipment, component cleaning, ordnance preparation, armament equipment servicing and limited general engineering. 322 Combat Support Squadron (CSS), which also resides at RBT, offers ground support services to the fighter squadron. 322 CSS activities therefore include operation of the fire station, maintenance of ground support equipment including fuel tankers, trucks and RAAF vehicles, fuel quality control laboratory, operation of fuel farms and aircraft refuelling operations, communications and radar, medical and dental facilities, messing facilities, Base police services and recreational facilities.


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2.4 Environmental ValuesThere are many environmental values at RBT which require management.

The main surface water body on the site – Four Mile Creek (otherwise known as Tindal Creek) – is a significant resource. There are also a number of sub-surface aquifers in the Tindal area, with the Tindall Limestone aquifer being the most significant. These resources are significant as they flow off-site, into the Katherine River. The River is used for a number of purposes including as a drinking water supply and for tourism and recreational activities. Potable water for RBT is provided by the Katherine River, however groundwater could be used as drinking water in the event of an emergency. Ground and surface water resources could be impacted via disposal of waste, including unauthorised dumping, leaks or spills of hazardous substances including fuel and chemicals, contaminated wastewater run-off from hardstand areas and washbays, ordnance detonation and fire training. All of these activities could also impact on the soil quality at the site.

Flora, fauna and their habitats have the potential to be impacted upon through human or animal activity including wildfire, chemical/fuel spills, weed infestation, indiscriminate waste disposal and feral animals. Although there are no plant species in the area classified as rare, threatened or endangered, there are some unusual and uncommon species in the region, including vegetation on limestone outcrops and plant species found in sinkholes of the karst landscape. There are also several rare and uncommon species of birds and mammals in the vicinity of RBT, including the Ghost Bat, Red Goshawk, Square-tailed Kite, Grey Falcon, Black Falcon (this is noted to be an endangered species), Black-tailed Cuckoo and Kultarr (a small carnivorous marsupial). Termite mounds present in the region are also significant and could be impacted upon.

There are no buildings, structures or sites at RBT which are registered with the NT National Trust or Australian Heritage Commission. There are, however, a number of archaeological sites of significance and Aboriginal sacred sites. Sacred sites are fenced and no disturbance has been recorded to date. Disturbance to sacred, significant and archaeological sites may occur as a result of new construction works or the various training activities undertaken at the Base.


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3. Environmental Management Program3.1 Legislation and Policy ObligationsDetails of the requirements of some of the key Commonwealth Acts applicable to the Base are detailed below. Further descriptions on other relevant legislative requirements is included in Appendix A – Environmental Legislation.

3.1.1 Commonwealth LegislationAccording to Defence Instruction (General) DI(G) ADMIN 40-1 – Environment and Heritage Protection, the principal Commonwealth legislation relating to environmental and heritage protection for the Department of Defence includes the Commonwealth Environment Protection and Biodiversity Conservation Act, 1999 (EPBC Act) and the Australian Heritage Commission Act, 1975. A brief discussion of the requirements of these Acts is detailed in Appendix A. Other Commonwealth legislation which may be applicable to activities undertaken at RBT are listed in Appendix A.

3.1.2 Territory LegislationAlthough many of the environmental principles by which Defence abides are based on Commonwealth environmental legislation, Territory (and State) legislation is still relevant to Commonwealth activities. The Defence Environmental Compliance Manual (1999) provides details on all Commonwealth and Territory (and State) legislation relevant to Defence activities.

The principal environmental legislation in the Northern Territory is the Waste Management and Pollution Control Act, 1998 (WMPC Act). The Act provides a broad and comprehensive tool for environmental management. Further details on this Act are contained in Appendix A. Other significant Acts include the Water Act, 1991,which aims to protect NT water resources and the Heritage Conservation Act, 1991,which specifies preservation requirements for areas deemed to be of historical interest or natural beauty.

The Territory Act which most closely resembles the Commonwealth EPBC Act is the Environment Assessment Act, 1982 which requires consideration of potential environmental effects in the formulation of proposals, carrying out of works and other projects. A brief description of this and other Territory legislation, which may be applicable for activities undertaken at RBT, is listed in Appendix A.

3.1.3 Defence Instructions and PoliciesThe Defence Environment Policy Statement was issued in 1998 and is authorised by the Chief of the Defence Force. It reflects the significance that the Government places on Defence’s role in protecting the environment. The Policy details environmental goals and principles to guide Defence in undertaking actions. The Policy is based on legislation and best practice. Defence’s environmental principles are encompassed within twelve environmental goals, which are:

manage the environment responsibly;conduct comprehensive environment impact assessments;comply with environmental legislation and policy obligations;conserve and manage renewable and non-renewable resources;


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conserve Australia’s natural and cultural heritage;conserve energy;minimise waste, control pollution and minimise and remediate contaminatedsites;consult effectively with the community;incorporate environmental considerations into purchase and procurementprocedures;minimise environmental impacts associated with military operations and training;incorporate environmental assessment into land disposal procedures; andconduct comprehensive environmental education and training for Defencepersonnel.

Environmental management is also guided by use of Defence Instructions (DIs) or Base Standing Orders (SOs). The DIs are not Base-specific and are adopted across all Defence sites. DIs are authorised by the Department of Defence in Canberra and are available for five key areas – administration, finance, logistics, operations and personnel. A list of relevant DIs dealing with environmental management at RBT is included in Appendix A. The SOs are site specific, with the OC 322 CSW (Combat Support Wing) responsible for ensuring these are kept up to date. Each SO is revised on a 12 monthly basis (approximately).

3.2 Responsibilities for Current Environmental Management

On a base level, the OC 322 CSW is responsible for managing base operations at RBT. The Commanding Officer of the Base Squadron (CO 322 CSS) is responsible to the OC for the day to day operation and safety of RBT. CO 75 SQN is responsible to OC 322 CSW for all base specific issues (including environmental issues), and is also responsible to OC 81 WG for other 75 squadron issues.

Environmental management responsibilities are also a responsibility of Corporate Services & Infrastructure Centre-Northern Territory/Kimberley (CSIC-NT/K). CSIC-NT/K incorporates three divisions - Infrastructure (ID), Service Delivery (SDD) and Information Systems (ISD) – however environmental management lies mostly with ID and SDD.

ID is responsible for overall estate planning and management, including EMPdevelopment. ID is specifically responsible for the provision of environmental advice, delivery of environmental works and consultancies and the issue of Environmental Certificates of Compliance (ECC) and other approvals. The Environment & Heritage section, comprising Environmental Officers (ENVIRO) and an Estate Environmental Manager (EEM), reside within ID.

SDD is responsible for the provision of a range of services to RAAF Base Tindal, including grounds maintenance, waste management, cleaning, catering and accommodation. These services are provided via the ‘Garrison Support” contract and other service contracts managed by SDD.

Executive and corporate support for Defence environment and heritage management is also provided through a series of organisations as detailed below.


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Regular monitoring and reporting of the EMP and its commitments will assist with assessment of impacts on the surrounding environment and determine the relevance/effectiveness of the Strategic Action Plans (Part A, Section 5.0) in meeting proposed environmental objectives. Monitoring and reporting will also enable regular review of the data so that continuous environmental improvement at RBT can be facilitated.

The Strategic Action Plans detail the responsibilities and processes for monitoring implementation of the EMP and regular reporting requirements. The type of monitoring required is considered appropriate to the nature, complexity and environmental significance of the activity.

3.4 Audit RequirementsTo assess whether the Strategic Action Plans are being implemented and that the environmental objectives are being met, it is necessary to undertake an audit program of the EMP on a periodic basis. Apart from verifying compliance with the EMP, the audits are also expected to identify any changes or additions to procedures that may be required to:

provide more efficient/effective ways of achieving environmental objectives;overcome environmental issues which have not yet been recognised; oradjust staffing or organisational arrangements.

As such, the audit program should be viewed as providing constructive criticism in environmental management at the Base and that its findings make a positive contribution to the achievement of environmental objectives.

An environmental audit consists of a systematic review and reporting process that involves interviews with Base staff, site inspections and review of data and records from monitoring programs.

The EMP is to be externally audited every five years. The audit is to be undertaken by external consultants, quality societies (eg Quality Assurance Services), or appropriate Defence personnel external to RBT.

The general steps in the environmental audit process, a brief description of each stage and responsibilities are shown in Table 3.2 – Stages in the Audit Process.


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environment. They also need to be aware of the Defence Environment Policy, relevant programmes designed to achieve objectives and operational procedures of the EMP that relate to their work. It is only by gaining confidence through appropriate training that personnel will become responsible and accountable for improving their own environmental performance.

Consultation of organisational charts to determine which employees have roles which could potentially impact on the environment is a starting point for identifying which personnel require environmental training. It is important that commanding officers, as well as contractors, are identified in this process, since they will also be working towards the objectives contained within the EMP. Any training offered needs to be targetted and of a suitable level for select small groups. An important mechanism to provide training will be the incorporation of environmental components into existing programs.

Induction training, providing an overview of Defence environmental objectives, shall be given to all staff, with more specific environmental awareness training provided to key staff and contractors. Further details of training requirements are provided within the Strategic Action Plans (Part A, Section 5.0).


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4. Environmental Objectives

4.1 IntroductionDefence’s environmental principles are encompassed within twelve environmental goals. These goals were listed in Section 3.1.3. Some of the principals included within these goals have been adopted as key environmental management objectives for RBT. These management objectives are presented below in a number of different performance areas.

4.1.1 Environmental Management SystemProvide broad environmental awareness training to all staff and more specifictraining to key staff and contractors to allow implementation of action plans andadherence to Commonwealth and Territory legislation.Facilitate continual improvement in environmental management by incorporatingappropriate monitoring and reporting, including audit and review of the EMP.Enable systematic environmental management by delineating responsibility forenvironmental actions.

4.1.2 Sustainable Use of the BaseMinimise waste generation through avoidance, reduction, re-use, recycling, andtreatment and ensure any waste disposed of is done so in an environmentallyresponsible manner, meeting legislative requirements as a minimum.Manage activities at the Base in order to maintain value of resources and optionsfor future land use. Where appropriate, rehabilitation or remediation of impactsis to be considered.

4.1.3 Pollution and Contamination Prevention and ManagementMinimise pollution to air, land and water through appropriate handling, storageand disposal of materials.Undertake assessment and remediation of contaminated sites, where necessary.

4.1.4 Natural Resource ConservationApply principles of water and energy conservation in line with operationalrequirements.Minimise impacts on native habitat to maintain their integrity, while consideringBase training and operational requirements.Ensure protection of native habitat and maintain biodiversity throughimplementation of natural resource management programs.

4.1.5 Heritage ManagementEnsure conservation and protection of places of heritage significance includingarchaeological sites and Aboriginal Significant and Sacred Sites.Manage heritage issues in consultation with stakeholders and authorities.


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4.1.6 Relationship with the CommunityMaintain Defence’s good neighbour policy incorporating community consultationand involvement, while being mindful of Defence’s security considerations.Address public concerns on environmental issues openly and effectively.


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5. Strategic Action PlansThis section presents the Strategic Action Plans (SAPs) required to achieve the environmental management objectives for the identified environmental issues at RBT. Based on the identified issues, the following SAPs have been formulated:

Fire ManagementWaste ManagementNoxious and Environmental Weeds and Feral AnimalsHazardous Materials ManagementWater ManagementSoil ManagementCultural HeritageSocial and Community IssuesFuel ManagementMosquito ControlFlora and Fauna and Habitat Management


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5.1 Fire ManagementSummary of IssuesAt least one wildfire occurs at Tindal annually. Frequent wildfires are a direct threat to flora and fauna and resulting biodiversity. They can result in significant and catastrophic impacts including loss of human life, asset damage, and impact on aircraft operations. Wildfires can generally be brought under control primarily due to the location of firebreaks. The firebreak network is therefore a vital asset in protection of the Base, its operations and the environment.

The current fire regime consists of a series of annual infrastructure and boundary protection burns undertaken in May/June. The program is also beginning to include wet and early dry season burns in an effort to reduce annual grasses and subsequent fuel loads, while providing a mosaic of burn patterns across the facility. The conduct of wet and early dry season burns is essential to minimise the risk of wildfire ignition, entry and/or spread within RBT.

It is critical that firebreaks are maintained at RBT and prescribed burns are undertaken annually to ensure adequate protection. Timing of controlled burns must be closely coordinated with aircraft activity to ensure safe outcomes. It is also essential that strategies on fire prevention and information on emergency response in the event of a fire are available to all personnel.

ObjectivesEstablish a fire regime that aims to protect personnel and property whilepromoting conservation of biodiversity and ecological integrity.Develop and document fire prevention strategies and emergency responseprocedures.

Monitoring/reportingMaintain records of prescribed burns on GISRecord number and location of wildfires annuallyReport all incidences of wildfire to RAAF Fire Brigade

Awareness/trainingEmergency fire training will be provided for all relevant personnel.Contractors undertaking burn-offs must be aware of aircraft flight programs andcritical timing issues. Close liaison with Base authorities is essential.Wildfire drills will be conducted annually.

References Section 3.12 in IER NT Bushfires Act, 1980DI(G) ADMIN 40-1 and DI(AF) LOG 9-2 – Environment and Heritage ProtectionDI(G) ADMIN 40-2 (draft) – Environmental ManagementFACMAN2 – Fire Management and the use of Halon GasesDefence Environment Policy Statement, 1998The Air Force Environmental Management Handbook


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5.2 Waste ManagementSummary of IssuesA variety of solid and liquid wastes are produced at RBT, including:

office-type waste (paper, packaging materials);kitchen waste;glass, bottles, cans (aluminium, steel);fluorescent light bulbs;general rubbish;building waste, including timber and plastics;garden refuse (cuttings, clippings);waste oil, fuel and solvents from servicing of vehicles, aircraft and othermachinery;waste cooking oil produced at the messes;photographic waste; andberyllium waste, produced from washing machine-gun components.

Quarantine waste, from overseas aircraft is also produced, albeit in small quantities.

Most waste is collected and disposed of off-site by Hannons Waste Disposals under contract to SDD. Very little waste is segregated and limited recycling is implemented at the Base. Some hazardous waste materials are not separated from the general waste stream, while other wastes, including medical waste, dog waste and sludge screenings, are incinerated. Waste management arrangements at RBT require improvement in terms of minimising waste generation, maximising recycling and/or re-use and appropriate treatment.

Unauthorised dumping of potentially contaminated waste in former borrow pits and burial of aircraft wreckage remains has occurred, with consequent soil and groundwater pollution a potential impact. Water pooling in dump sites has proven to be a good mosquito breeding habitat. Green waste has been disposed of in unauthorised areas and has resulted in propagation of weeds. An approved waste transfer station is being developed near the married quarters to facilitate off-site waste disposal.

The fire training area has been used for disposal of general rubbish, including scrap metal and drums, however some items such as car bodies are used a fire training tools. There has also been unauthorised disposal of oil and fuel into the evaporation pitsassociated with the training area.

RBT operates a sewage treatment plant. The plant produces sludge screenings, sewage sludge and treated wastewater. The wastewater is disposed of by irrigation of the nearby ‘horse paddock’, whilst screenings are incinerated and sewage sludge is excavated and disposed of according to current requirements. Sludge has been spread over the horse paddock in the most recent round of maintenance. A number of septic tanks are also in operation at RBT. None of the tanks appears to have been maintained since development of RBT, although a holding pit, located near the golf course, is pumped out by Hannons during peak times and the waste disposed of off-site.


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5.3 Noxious and Environmental Weeds and Feral Animals Management

Summary of IssuesThere are currently a variety of noxious and environmental weed species at RBT which are widespread. These include:

Caltrop (Tribulus terrestris) – declared Class B;Rubber bush (Calotropis procera) – declared Class B;Sicklepod (Senna obtisifolia);Khaki weed (Alternanthera pungens) – declared Class B; andMission grass (Pennisetum polystachion) – declared Class B.

Of these species, Caltrop and Rubber bush are the most prevalent. The primary reasons for weed spread and/or establishment within RBT has been due to inappropriate disposal of green waste and general disturbance to soil and vegetation, including cleared areas such as borrow pits and tracks, and along side drains. Vehicle movement within and from outside RBT may have also exacerbated weed spread through the translocation of weed seed upon vehicle parts.

Poor waste disposal practices around RBT has proved to be a food source for feral animals. Feral cats are noted to live in the stormwater drains and search for food from bins stored near the messes. Other feral animals known to exist on RBT are donkeys and buffalo, however their numbers are not significant. Cane toads have recently arrived in the Katherine region and are increasing in numbers. Feral animals can exacerbate damage to vegetation and soil, or have a direct impact on native fauna (cane toads and feral cats). Feral animals may also represent a generic health risk to both native fauna and Base personnel.

In the south-eastern sector of the base, grazing of cattle has been allowed, however this is no longer an approved activity.

Invasion by both noxious weeds and feral animals can be a threat to biodiversity at RBT, affecting flora, fauna and their habitats.

ObjectivesMinimise the introduction and spread of noxious and environmental weeds.Control feral animals on RBT to minimise their impact on the environment.

Monitoring/reportingReport and record sightings of feral animals to CSIC-NT/K ID ENVIROMonitor progress of weed and feral animal eradication programs over time,including quantity and type removed and location

Awareness/trainingContractors undertaking weed and feral animal management shall beappropriately experienced and qualified/licensed in weed recognition, poisons handling and firearm use as appropriate.Posters highlighting weed management initiatives and high priority species to bedisplayed in public areas.


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5.4 Hazardous Materials ManagementSummary of IssuesA variety of hazardous materials are stored, handled and transported at RBT. The two main chemical storage areas are the 322 CSS K Group and the 75 Squadron K Group. Substances held in these areas include oils, greases, solvents, gases (acetylene, LPG etc.), adhesives, paints and pesticides. Very few spills have been reported at RBT, however the volume and types of material available on site, coupled with the sensitive Tindall limestone landscape, carries a significant environmental risk.

Poor hazardous materials management can result in accidents to users or spills resulting in soil, surface and/or groundwater contamination. Appropriate storage of chemicals, maintenance of storage and handling equipment and supply of response equipment is imperative to minimise the likelihood and consequence of a hazardous event. Maintenance and promulgation of emergency response procedures, including the use of spill kits and incident notification protocols, are essential.

Inventories of chemicals stored and of equipment containing hazardous materials, such as ozone depleting substances or PCBs, are limited. Tracking chemical usage and labelling of equipment aids in the efficient management of hazardous materials and provides useful information for disposal, clean-up or in an emergency event.

ObjectivesPrevent pollution of the RBT environment by the release of hazardous materialsduring storage, handling and transport.

Monitoring/reportingReport and record incidences of all hazardous materials incidentsMonitor effectiveness of bunding and interceptors under wet and dry seasonconditions

Awareness/trainingConduct emergency response training, including drills, for all personnelConduct appropriate hazardous material training for operational staff.

References Section 3.9 in IERNT Dangerous Goods Act, 1998NT Work Health (Occupational Health and Safety) Regulations, 1996NT Waste Management and Pollution Control Act, 1998DI(G) ADMIN 40-1 and DI(AF) LOG 9-2 – Environment and Heritage ProtectionDI(G) ADMIN 40-2 (draft) – Environmental ManagementDI(G) ADMIN 40-3 (draft) – Contamination Prevention and ManagementDI(G) LOG 07-8 and DI(AF) LOG 16-1- Management of Hazardous Substances Except Dangerous Goods in Class 1 (Explosives) and Class 7 (Radioactive Materials)DI(AF) LOG 9-7 - Management of Ozone Depleting Substances in the Defence OrganisationDI(G) LOG 10-3 (AF 9-8) – Management of Ozone Depleting Substances in Logistic ApplicationsDI(AF) PERS 56-6 – Management of Hazardous Wastes and Hazardous Discharges – Environmental Health Aspects


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5.5 Water ManagementSummary of IssuesWater resources at RBT include Tindal Creek and the Tindall limestone aquifer. Water from both of these ultimately discharges into the Katherine River, which is a potable water supply for the area. Contaminated wastewater is generated at RBT from a number of activities, including vehicle and aircraft washing, steam cleaning and degreasing of engines. In some cases it is discharged directly into the stormwater system. Numerous depressions and sinkholes at the Base significantly increase the risk of wastewater/stormwater directly entering groundwater. Figure 3 - Stormwater Drainage at RAAF Base Tindal shows the directions in which stormwater flows off-site. Capture and appropriate disposal of pollutants is essential to protect the area’s important water resources.

Stormwater drains, when inadequately maintained, have caused flooding and associated problems, including mosquito breeding and increased avian activity, resulting in increased birdstrike incidents.

Limited surface and groundwater sampling is undertaken at RBT. A sound water quality sampling regime is essential to ensure that environmental impacts are being minimised and water resources adequately protected.

Water is sourced from both town supply and groundwater. Efficient use of water resources require harnessing.

ObjectivesMinimise the release of contaminants to receiving surface and ground waters.Implement water conservation measures consistent with operational andfunctional requirements.

Monitoring/reportingMonitor quality of groundwater and surface water in high risk receivingenvironmentsMonitor condition of earthen drainsRecord and track water usage

Awareness/trainingContractors engaged in water sampling must be aware of correct samplingtechniques.

ReferencesSections 2.5.5, 2.5.6, 3.6.1.4, 3.6.2 in IERNT WMPC Act, 1998NT Water Act, 1991DI(G) ADMIN 40-1 and DI(AF) LOG 9-2 – Environment and Heritage ProtectionDI(G) ADMIN 40-2 (draft) – Environmental ManagementDI(G) ADMIN 40-3 (draft) – Contamination Prevention and ManagementDefence Environment Policy Statement, 1998Air Force Environmental Management Handbook


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5.6 Soil ManagementSummary of IssuesMost of the soils within the area of the Base are not highly susceptible to erosion. Terrain gradients are such that surface water flow and soil transport is slow. Sub-surface soils show a slight tendency towards surface gully erosion. Grey-brown clays - located upon broad alluvial back plains, in some drainage floors and locally in small depressions - represent the most poorly drained soils in the area and they become more susceptible to erosion when they are waterlogged.

Minor-moderate soil erosion at RBT is occurring in a number of areas and can occur as a result of a variety of activities. Damage to vegetation cover, which is exacerbating soil erosion, is being caused by both human disturbance (i.e. land clearing for fire breaks, Army exercises and Base combatant/defence duties) and by animal disturbance from unauthorised grazing by cattle or feral animal activity. Earthen stormwater drains are also being eroded due to poor maintenance. Soil erosion from human and animal disturbances may impact on downstream water quality, cause silting of sinkholes or localised flooding and may reduce land use accessibility. The health and habitat of sensitive flora and fauna may also be compromised. Maintenance of existing drainage patterns and minimisation of exposure of sub-surface soils will minimise soil erosion.

ObjectivesMinimise disturbance of soils by Base and natural activities.Minimise the progress of erosion from stormwater drains, natural drainage linesand disturbed areas.

Monitoring/reportingMonitor disturbed areas, particularly favoured training areas, for acceleratederosionInspect earthen drains for maintenance requirements

Awareness/trainingContractors/personnel involved in training/operational activities made aware ofsoil erosion potential and appropriate mitigation measures.

ReferencesSections 2.5.4, 3.4.3, 3.6.1.9, 3.6.2 in IERCommonwealth Environment Protection and Biodiversity Conservation Act, 1999NT Soil Conservation and Land Utilisation Act, 1970 NT Water Act, 1991DI(G) ADMIN 40-1 and DI(AF) LOG 9-2 – Environment and Heritage ProtectionDI(G) ADMIN 40-2 (draft) – Environmental ManagementDefence Environment Policy Statement, 1998Air Force Environmental Management Handbook


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5.7 Cultural HeritageSummary of IssuesAboriginals have long used the Katherine/Tindal area as a hunting and gathering region. Many plant and animal species in the area have been, and still are, a favoured part of the local Aboriginal diet. There are many sites within the region which indicate prolonged habitation.

Archaeological and anthropological assessments undertaken in the early 1980s identified forty-six sites of archaeological significance at RBT. The assessment identified two significant Aboriginal sites, with another two sites only recently identified. A map showing the location of all 46 sites could not be found, with data for only 41 sites available. Figure 4 – Archaeological Sites of Significance shows the location of the 41 sites and the four significant Aboriginal sites. The significant Aboriginal sites include:

Jiberm (site 38 on map), which has been registered with the Aboriginal AreasProtection Authority as a sacred site and is fenced and signposted. This site is a Jaowyn site; Latbulluk (site 32 on map), which is not a registered site but is a recorded sacredsite and is also fenced; andanother two recorded Aboriginal sacred sites (located near Stuart Highway, eastof Base), which are neither registered nor fenced.

Artefacts were found, the most common being open sites in the form of scatters of stone artefacts but also including shelters with occupational debris, quarries, knapping floors, rock art and other sites. Sites are generally clustered around sandstone outcrops and along creeklines

Inadequate mapping and placarding/fencing of sites could result in disturbance or damage from construction and development works or during Base training and operational exercises. Commitment to identification and conservation of heritage sites is essential to ensure appropriate management of cultural heritage at RBT.

Sinkholes in the region contain unusual vegetation described as mesophyll vine forest. These are tree and fruit species which are fruit-producing and would have been a valuable resource to the local Aboriginals. Other plant species in the sinkholes have possible pharmaceutical or poisonous properties, both of which may have had a significant role in indigenous hunting-gathering activities.

ObjectivesProtect cultural heritage values at the Base and make provision for involvementof Aboriginals in management of sacred sites.

Monitoring/reportingReport any new sites or findings of surveys to AAPA/DLPEMonitor registered and recorded sites for unauthorised disturbance

Awareness/trainingContractors and personnel undertaking works at site must be aware of heritagemanagement objectives, including the location of significant sites, when in close proximity to the work area.


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5.8 Social and Community IssuesSummary of IssuesThere are very few concerns with the relationship Defence has with the Katherine community. Since inception of the Base in the late 1980s, RAAF personnel have integrated well into the local community. As part of Defence’s good neighbour policy, regular contact has been maintained with community leaders and Aboriginal community representatives. Local community groups are kept informed of relevant Base activities and Aboriginal groups have requested, and been granted, access to sacred sites.

Principles of environmental compliance and accountability have been adopted and any complaints received with respect to environmental issues (eg aircraft noise) are promptly dealt with. Complaints are directed to RAAF Security Police, documented and then forwarded to the CO 322 CSS. The complaint is investigated and followed up until all parties are satisfied.

The base boundary is not completely fenced, and where existing is historical and in some areas is in poor condition. Signage is provided along some sectors of the fence.

ObjectivesMaintain regular liaison with the local community thereby ensuring they are fullyaware of Base activities and promptly address any public concerns and complaints.Minimise impact of Base activities on adjacent land and water users.

Monitoring/reportingRecord number and type of public complaints in a register and report on howissues were resolved

Awareness/trainingN/A

ReferencesSections 3.3.3, 3.11 in IERDI(G) ADMIN 40-1 – Environment and Heritage ProtectionDI(AF) OPS 3-7 – Aircraft Noise DisturbanceDI(AF) PERS 60-8 – Air Force Management and OHS Management Structure and FunctionsDI(AF) OPS 5-22 Security Fencing of Royal Australian Air Force BasesNT Draft WMPC (Environmental Noise) Regulations, 1999 (yet to be promulgated)Defence Environment Policy Statement, 1998Air Force Management Handbook


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5.9 Fuel ManagementSummary of IssuesRBT has two major fuel farms consisting of fourteen tanks embedded into an aboveground mound. Both fuel farms store Avtur, for aircraft. There are also a number of above and underground fuel storage tanks which store petrol and diesel, for vehicles and other machinery. Mobile fuel tankers, stored in the parking area next to Fuel Farm 1, are used to refuel the aircraft. Both fuel farms have evaporation/detention ponds which collect potentially contaminated stormwater and fuel spills/leaks. The ponds are a vital asset in the prevention of soil and groundwater contamination. It is therefore imperative that they are regularly maintained. To further ensure protection of the environment, it is also essential that personnel are trained in the use of emergency response equipment, including spills kits, and are aware of notification procedures.

Leaks from the underground fuel storage tanks in the mid 1990s resulted in a major tank replacement program but no associated remediation works. No integrity or pressure testing of these tanks occurs but reconciliation of fuel bought and used occurs daily. Aboveground fuel storage tanks (which hold up to 5,000L of diesel) are not bunded which is a moderate risk to the environment.

ObjectivesPrevent the release of fuels to the environment during storage, handling andtransport.

Monitoring/reportingMonitor evaporation ponds and fuel interceptors regularly to determine operationand maintenance requirementsMonitor fuel consumption from underground fuel storage tanks on daily basis andproduce weekly reconciliation reports Report all incidences of leaks/spillsMonitor water from bores located adjacent to fuel storage areas and Tindal Creekfor hydrocarbon contamination

Awareness/trainingEmergency response training, including drills, for all relevant personnel will beprovided.

ReferencesSection 3.10 (including subsections) in IERNT WMPC Act, 1998NT Water Act, 1991AS 1940-1993 Storage and Handling of Flammable and Combustible LiquidsDI(G) ADMIN 40-1 and DI(AF) LOG 9-2 – Environment and Heritage ProtectionDI(G) ADMIN 40-2 (draft) – Environmental ManagementDI(G) ADMIN 40-3 (draft) – Contamination Prevention and ManagementDI(AF) AAP 7743.001-6 – Aviation Fuel InstallationsDI(AF) AAP 3504.001 – Hazardous Goods Management ManualDI(G) LOG 07-8 and DI(AF) LOG 16-1 – Management of Hazardous Substances Except Dangerous Goods in Class 1 (Explosives) and Class 7 (Radioactive Materials)Defence Environment Policy Statement, 1998Air Force Environmental Management Handbook


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5.10 Mosquito ControlSummary of IssuesMosquito surveys undertaken at Tindal have identified a number of species that have the potential to become significant pests in the area if appropriate measures are not taken to minimise their spread. Mosquito management is required to mitigate the spread of disease. A large number of overseas aircraft land at Tindal as the first Australian port of call. It is therefore, also important that WHO regulations applicable to international transit zones are complied with.

Surveys at the Base have identified potential breeding sites for pest and disease carrying mosquito species. Potential breeding sites include the network of open unlined drains, the sewage ponds and borrow pits. Various artificial water holding receptacles, such as tyres and drums, are also potential breeding sites. Borrow pits and drains require appropriate maintenance to ensure free flowing of water.

Mosquitoes favour stagnant, nutrient enriched water as breeding habitat and minimisation or remediation of conditions is essential to safeguard health. A monitoring program is in place and is essential in the early detection of pest species.

ObjectivesMinimise the creation of mosquito breeding habitat.Undertake a mosquito monitoring program and implement appropriate controlmeasures to eliminate populations or breeding conditions when required.

Monitoring/reportingMonitor surveillance traps and report to THS Entomology Branch on anyidentified exotic species

Awareness/trainingN/A

ReferencesSection 3.4.5 in IERDI(AF) PERS 22-3 – Quarantine Clearance of Aircraft Arriving at RAAF Bases from OverseasDI(AF) PERS 56-1 – Environmental Health ServicesDefence Environment Policy Statement, 1998Airforce Environmental Management Handbook


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5.11 Flora and Fauna and Habitat ManagementSummary of IssuesMost of the area around the Base is covered with mixed eucalypt woodland and open forest. There are no plant species in the area classified as rare, threatened or endangered, however there are some unusual species in the region, including vegetation on limestone outcrops and mesophyll vine forests found in sinkholes. Within the region the black falcon is the only species noted to be endangered. There are some rare and uncommon fauna present, including the Ghost Bat, grey falcon, red goshawk and Kultarr. Termite mounds are also prevalent throughout the Katherine/Tindal area, and are of significance.

Many activities undertaken at RBT have the potential to impact on native flora and fauna and the integrity and biodiversity of native habitat areas. Damage to vegetation by human and animal disturbance, wildfire, weed spread through inappropriate disposal practices and planting of non-native species all contribute to compromising the habitats for native flora and fauna. General contamination and pollution can also impact on native habitats.

There are records of fauna being killed as a result of Base operations, with goannas, wallabies and other wildlife falling into the fire training pit and birds dieing as a result of collisions between birds and aircraft (birdstrike).

Birdstrike is a significant issue at Tindal. Burning off attracts birds due to the large number of insects in the air during this time. Birds are also attracted to ponds and irrigation areas, particularly in the dry season. It is important that birdstrikes are minimised to ensure safety of aircraft and personnel in addition to the conservation of rare bird species.

ObjectivesMinimise effects on native flora, fauna and habitat areas.

Monitoring/reportingRecord details on frequency and nature of birdstrikesRecord sensitive flora and fauna sites on GISMonitor cleared areas of habitat

Awareness/trainingSensitive habitat areas to be promulgated to all personnel.

ReferencesSections 2.6 (including subsections), 3.4.2, 3.4.3, 3.4.3 in IERCommonwealth Environment Protection and Biodiversity Conservation Act, 1999NT Soil Conservation and Land Utilisation Act, 1970NT Noxious Weeds Act, 1963NT Parks and Wildlife Act, 1977 DI(G) ADMIN 40-1 and DI(AF) LOG 9-2 – Environment and Heritage ProtectionDI(G) ADMIN 40-2 (draft) – Environmental ManagementDI(G) ADMIN 40-3 (draft) – Contamination Prevention and ManagementDefence Environment Policy Statement, 1998Air Force Environmental Management Handbook


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PART B – Implementation Plan

Introduction

The Implementation Plan is a structured schedule for implementation of specific tasks and improvements to achieve the environmental objectives detailed in the Strategic Action Plans. The plan identifies the priority, responsibilities, budgetary information and timeframes for each task to be undertaken so that the objectives are met.

For simplicity, the plan has been split into a series of tables, each of which correspond to the Strategic Action Plans discussed in Part A of this EMP. The tasks to be undertaken for each plan are included in the table, along with other information, thereby making the plan an effective working management tool that can be easily used by the relevant facility manager and continuously reviewed and updated.


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Appendix A Environmental Legislation


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The following lists of environmental legislation are not intended to be a thorough review of all Commonwealth or NT environmental regulations but concentrate on Acts and regulations applicable to activities undertaken at RAAF Base Tindal.

Commonwealth Legislation

Aboriginal and Torres Strait Islander Heritage Protection Act, 1984The Act describes requirements in relation to preservation of objects of significance to Aboriginals and Torres Trait Islanders.

Australian Heritage Commission Act, 1975The Act describes the requirements for preservation of the natural environment. The Act sets up the Register of the National Estate (RNE) which is a register listing buildings or other items of architectural or cultural heritage, natural heritage or Aboriginal cultural heritage value. Value can be assessed as being aesthetic, historic, scientific or social. Under the Act, no action can be taken which adversely affects a place on the RNE (or on the Interim List of the RNE). Places could include national parks, nature reserves, Aboriginal sites of significance, archaeological sites, historical buildings and other conservation areas.

Endangered Species Protection Act, 1992The Act was replaced by the Commonwealth Environment Protection and Biodiversity Conservation Act, 1999. It specified requirements for protection of endangered species.

Environment Protection (Impact of Proposals) Act, 1974The Act was one of the Commonwealth’s prime pieces of legislation, focusing on the environmental impact of new proposals. The EPIP Act was replaced (on 16th July,2000) by the Commonwealth Environment Protection and Biodiversity Conservation Act, 1999 (EPBC Act). As well as incorporating the EPIP Act, the new EPBC Act replaces the Endangered Species Protection Act, 1992, The National Parks and Wildlife Conservation Act, 1975, World Heritage Properties Conservation Act, 1983and the Whale Protection Act, 1980.

EPBC Act, 1999Just like the old EPIP Act, the EPBC Act describes the requirements for assessing whether a project, development or activity will impact on the environment. Hence, its main intention is to promote sound planning by ensuring that all environmental matters for a new project are considered. The primary objective of the Act is to promote the conservation of biodiversity through the identification of key threatening processes and preparation of abatement plans.

National Parks and Wildlife Conservation Act, 1975The Act was replaced by the Commonwealth Environment Protection and Biodiversity Conservation Act, 1999. The Act specified requirements for the protection, conservation and management of wildlife in areas under Commonwealth jurisdiction.


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Northern Territory Legislation

Aboriginal Sacred Sites Act, 1989The Act describes requirements in relation to preservation of objects of historical or anthropological significance.

Bushfires Act, 1980The Act provides the power to direct landowners in taking precautions to prevent bushfires and provides measures in controlling bushfires.

Dangerous Goods Act, 1998The Act discusses the requirements of handling, transportation, storage, use and disposal of all hazardous or dangerous goods. The Act is not applicable in relation to radioactive substances.

Environmental Assessment Act, 1982The Act requires that potential environmental effects need to be considered in theformulation of proposals, carrying out of works and other projects and enforcement of agreements and arrangements.

Heritage Conservation Act, 1991The Act specifies preservation requirements for areas deemed to be of historical interest or natural beauty.

Noxious Weeds Act, 1963The Act discusses eradication and control of noxious weeds.

Ozone Protection Act, 1990The Act regulates manufacture, sale, distribution, use, recycling, storage and disposal of stratospheric ozone depleting substances or articles which contain these substances. The WMPC Act, 1998 indicates that the Ozone Protection Act is repealed and will be incorporated into the WMPC Act in due course.

Public Health Act, 1952The Act discusses water quality protection, waste management and air pollution. It gives details on the transportation and disposal of wastes – mainly from noxious trades.

Soil Conservation and Land Utilisation Act, 1970The Act discusses soil conservation, land reclamation, and prevention and remediation of soil erosion.

Territory Parks and Wildlife Conservation Act, 1977The Act specifies conservation of flora and fauna through declaration of land as a reserve.

Waste Management Pollution Control Act, 1998The main objectives of this Act are:…(a) to protect, and where practicable to restore and enhance the quality of, the Territory environment by-


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(i) preventing pollution;(ii) reducing the likelihood of pollution occurring;(iii) effectively responding to pollution;(iv) avoiding and reducing the generation of waste;(v) increasing the re-use and re-cycling of waste; and(vi) effectively managing waste disposal.

(b) to encourage ecologically sustainable development; and(c) to facilitate the implementation of national environmental protection measures made under the National Environment Protection Council (Northern Territory) Act.

Water Act, 1991The Act specifies what constitutes environmental harm to NT water resources as well as providing guidance on investigation, protection and administration of water resources.

Northern Territory Regulations

NT Draft Waste Management and Pollution Control (Environmental Noise) Regulations, 1999These regulations specify general maximum noise pollution levels, procedures for application for permission to cause noise emission, specific maximum noise pollution levels, noise measurements and procedures for notification and review.

Work Health (Occupational Health and Safety) Regulations, 1996The regulations contain obligations with respect to having a safe working environment. They discuss workplace issues including working in confined spaces and with hazardous substances. Also includes what constitutes personal protective equipment.


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Defence Instructions

These Defence Instructions are applicable to environmental-related issues only. The list does not represent all the available instructions.

DI(AF) AAP 3431.001 – Manual of PurchasingDI(AF) AAP 3504.001 – Hazardous Goods Management ManualDI(AF) AAP 7743.001-6 – Aviation Fuel InstallationsDI(AF) LOG 16-101 – Explosive Ordnance and Associated Equipment DI(AF) LOG 16-1 and AAP 3504.001 – Ordering and Procurement of Supplies Containing Hazardous MaterialsDI(AF) OPS 3-7 – Aircraft Noise DisturbanceDI(AF) PERS 56-1 – Environmental Health ServicesDI(AF) PERS 22-3 – Quarantine Clearance of Aircraft Arriving at RAAF Bases from OverseasDI(AF) PERS 56-6 – The Management of Hazardous Wastes and Hazardous Discharges – Environmental Health AspectsDI(AF) PERS 56-8 – Aerial Application of PesticidesDI(G) ADMIN 40-1 and DI(AF) LOG 9-2 – Environment and Heritage ProtectionDI(AF) PERS 60-10 (OH 15 only) (DI(G) ADMIN 40-2 Draft) – Environmental Management (in conjunction with DI(G) ADMIN 40-1 promulgates Defence policy on the environmental management of Defence facilities and property)DI(G) ADMIN 40-3 (draft) – Contamination Prevention and ManagementDI(G) ADMIN 44-1 and DI(AF) LOG 9-7 - Management of Ozone Depleting Substances in the Defence OrganisationDI(G) LOG 01-4 and DI(AF) LOG 16-8 – Safety Policy for the Transport of Ammunition and ExplosivesDI(G) LOG 01-4 and DI(AF) LOG 16-9 – Safety Principals for the Storage of Ammunition and ExplosivesDI(G) LOG 07-8 and DI(AF) LOG 16-1 – Management of Hazardous Substances Except Dangerous Goods in Class 1 (Explosives) and Class 7 (Radioactive Materials)DI(G) LOG 10-1 (AF 9-5) – Dumping of Surplus and Obsolete Stores and Material at SeaDI(AF) LOG 4-8 – Disposal of StoresDI(AF) LOG 07-05 - Disposal of Stores Other than WeaponsDI(G) LOG 10-2 (AF 9-6) – Management of Land Affected by Unexploded Ordnance (UXO)DI(G) LOG 10-3 (AF 9-8) – Management of Ozone Depleting Substances in Logistic ApplicationsDI(G) PRS 19-3 (AF 56-13) – Occupational Health and Safety – Radio Frequency Radiation HazardDI(G) PERS 40-1 (AF 56-24) – Asbestos Management in the ADF and the Department of DefenceDI(G) LOG 07-11 - Lithium Batteries, Policy for Acquisition, Storage, Transport and DisposalDI(AF) PERS 60-8 – Air Force Management and OHS Management Structure and Functions


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Documents

Item 02. Environmental Management Plan for RAAF Base