 Commonwealth of Australia 2010


Heap leach operation and management



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81.1Heap leach operation and management


Whereas there have been numerous heap leach operations in North America and elsewhere, this technique has had relatively little use in Australia (Section 5.2.2). No published guidance is available specifically on the management of heap leach operations in Australia, though a range of general guidance documents on cyanide management is available. Information for heap leach operations is available from various sources overseas.

Thiel and Smith (2003) identify a range of potential environmental risk issues associated with geotechnical aspects of heap leach operations (Table 11.).

Table 11.. Summary of key concerns of heap pads and heaps


Performance Area

Key Concerns

Slope stability

Global and deep-seated failures due to extreme heights and base pressures




Sliding block stability along geomembrane interfaces




Effects of active leaching, with elevated degrees of saturation




Long-term chemical and biological degradation of ore




First-lift stability affected by lift thickness (5 m to 50 m) and stacking direction




Drain pipe failure

Liquefaction

Earthquake-induced failures




Possible static liquefaction flow slides

Water management

Tropical installations can have large surplus water balances




Designs include interim catch benches and temporary caps




Phreatic levels range from 1 to 60 m over the base liner

Liner durability and leakage

Coarse rock ‘overliner’ systems and liner puncture

Extreme pressures caused by weight of heap and equipment




Durability against chemical attack – especially for 96% H2SO4 (for copper operations)




Valley fill systems create very high solution levels

* Source: Thiel and Smith (2003).

81.2Cyanide waste management

81.2.1International requirements for cyanide waste management


International requirements for the management of cyanide-containing wastes are incorporated in various Conventions to which Australia is a signatory.

The Basel Convention aims to protect the environment and human health from the improper disposal of hazardous wastes (Department of Foreign Affairs and Trade, 1992). The Basel Convention has three key objectives:



  • to minimise the generation of hazardous wastes;

  • to ensure the availability of adequate disposal facilities for the environmentally sound management of hazardous wastes; and

  • to reduce transboundary movements of hazardous wastes to a minimum consistent with their environmentally sound and efficient management.

Cyanide-containing wastes from heat treatment and tempering operations (Y7), inorganic cyanides (Y33) and organic cyanides (Y38) are classified as Hazardous Wastes (Annex 1) in the Basel Convention (Department of Foreign Affairs and Trade, 1992).

No organisations have been authorised to export cyanide-containing wastes from Australia.

Under Article 11 of the Basel Convention, Parties to the Convention may enter into bilateral, regional or multilateral agreements or arrangements with non-Parties provided these agreements or arrangements conform to the environmentally sound management of such wastes as required by the Convention. Australia is a signatory to two such multilateral agreements including:


  • Organisation for Economic Cooperation and Development Control System. The OECD has special rules for shipments of waste for recovery purposes. The rules mean that waste can be shipped between OECD countries, even if they are not Parties to the Convention.

  • Waigani Convention. A convention to ban the importation into forum island countries of hazardous and radioactive wastes and to control the transboundary movement and management of hazardous wastes within the South Pacific region (Department of Foreign Affairs and Trade, 2001).

The Basel Convention and associated Conventions are implemented in Australia through the Hazardous Waste (Regulation of Exports and Imports) Act 1989 (Cwlth), administered by DEWHA.

81.2.2Sea dumping of cyanide wastes


DEWHA administers the Environment Protection (Sea Dumping) Act, (1981), which ratifies the International Protocol relevant to the Act - Protocol for the Convention on the Prevention of Marine Pollution Dumping of Wastes and Other Matter (London Convention) (Department of Foreign Affairs and Trade, 1985). The Act provides for the regulated disposal of wastes and other substances in waters off Australia and its External Territories. The International Maritime Organisation (IMO) has Secretariat responsibilities for the London Convention and Australia is a member of the IMO.

Australia is a signatory to the 1982 United Nations Convention on the Law of the Sea, which includes measures to prevent, reduce and control pollution of the marine environment by dumping of wastes (Department of Foreign Affairs and Trade, 1994).

More recently, Australia has implemented the 1996 Protocol to the Convention on the Prevention of Marine Pollution by Dumping of Wastes and Other Matter, 1972. The 1996 Protocol to the London Convention severely restricts the list of substances that may be disposed of at sea.

Australia is a signatory to the Protocol for the Prevention of Pollution of the South Pacific Region by Dumping (Department of Foreign Affairs and Trade, 1986), which provides that all appropriate measures are taken to prevent, reduce and control pollution in the Protocol Area by dumping of wastes at sea.

Examples of state legislation pertaining to sea dumping of wastes include the Environment Protection (Sea Dumping) Act, 1984 (SA), the Marine Pollution Act, 1987 (NSW), the Marine (Sea Dumping) Regulations, 1982 (WA), and the Transport Operations (Marine Pollution) Regulations, 1995 (Qld).

DEH/DoD (2003) provide a historical account of 39 recorded events involving the disposal of cyanide salts or cyanide-containing wastes in Australian oceanic waters occurring between 1979 and 1953. Waste types disposed at sea were described variously as sodium cyanide, cyanide residues, alkaline cyanide solution, neutralised electroplating vat waste, carbonate/cyanide, pots, cyanogen bromide, cyana-gas or heat treatment salts. Records indicate ~80 000 L was disposed of at sea, plus three disposal events involving a total of ~26 tonnes of cyanide wastes (typically in drums) and 19 cyanide-impregnated vats. Wastes were disposed of offshore from New South Wales, South Australia, Queensland, Victoria and Tasmania. BRS (2002) also describe cyanide waste disposal in the 1970’s into south east Australian marine waters (1500 m depth).

There have been no reported instances of sea dumping of cyanide-containing wastes in Australian waters since 1979 and since the inception of the Environment Protection (Sea Dumping) Act, (1981), which strictly prohibits the disposal of chemical wastes at sea.

81.2.3Trans-national waste movement


Domestic movement of controlled waste, including cyanide-containing wastes between states and territories is managed through the National Environment Protection Measure (NEPM) Movement of controlled waste between states and territories (NEPC, 1998).

Cyanide wastes are controlled wastes under the NEPC (1998) NEPM. The NEPM provides a comprehensive, national system for monitoring and reporting all interstate movements of controlled waste. The system ensures that the controlled waste reaches the approved facilities for treatment, recycling, storage and/or disposal and thereby aims to minimise impacts to the environment and human health. Under the system, the waste producer is required to apply for a consignment authorisation number through the state or territory environment protection agency of the wastes destination. The producer is issued with a unique authorisation number for the type of controlled waste, their nominated licensed transporter and their nominated licensed waste facility.

A record is kept of each shipment of controlled waste by using a 5 docket Waste Transport Certificate available from the producer's state or territory environment protection agency. The waste producer, waste transporter, operator of the disposal facility and governments of the generating, receiving and any transit states or territories are informed about each shipment. The information gathered assists in dealing with emergency situations and in gaining a better overall understanding of the movement of controlled wastes between states and territories.

81.2.4States and territories waste management


Each Australian state and territory provides statutory controls on waste generation and management (refer Table 11.). Requirements are established for cyanide-containing substances that are classified as wastes to be handled and disposed of by licensed waste disposal or treatment contractors/facilities in accordance with state, territory and National legislation and policies. Due to their toxicity, cyanide-containing wastes are stringently regulated. In NSW, cyanide wastes are managed in accordance with the Environmental guidelines: assessment, classification and management of liquid and non-liquid wastes (NSW EPA, 1999). Such wastes are usually treated by means of chemical destruction (liquids) using sodium hypochlorite or chemical fixation (non-liquids) using cement or similar products. Electroplating sludges derived from plating facilities are stabilised as filter cake and/or solidified. Subject to passing leachate testing requirements, the waste is disposed of at a Solid Waste Class 2 Landfill with a currently operating leachate management system. Waste from heat treatment facilities can be in the form of sand and slag aggregate, which is usually treated prior to disposal.

The three major sodium cyanide manufacturing facilities in Australia produce gaseous, liquid and solid wastes containing the cyanide compounds. Product is recovered where practical within the processes and re-used and/or treated by various means to constituent by-products. Wastewater discharges and air emissions are monitored and environmental emissions typically only occur under license (e.g. trade waste agreements, permits) authorised by various state and territory environment protection agencies. The manufacturing facilities typically collect/recycle packaging materials, such as bulk bags, supplied to customers.

Mining wastes containing cyanide include tailings, which are emitted to land in TSFs. There, reactions occur leading to the volatilisation of much of the cyanide to the atmosphere, or other attenuation processes (e.g. complexation, biodegradation; refer Section 23.3). Cyanide destruction processes are implemented prior to the point of discharge at some mines. Recycling of cyanide solutions also occurs in order to minimise chemical costs and conserve water, which is typically associated with cyanide wastes. Containers used to store and transport sodium cyanide are generally returned to the manufacturer, and some packaging materials are disposed of in TSFs.

Table 11.. Primary state and territory waste management legislation and guidance



State/Territory

Relevant Waste Management Legislation/Guidance

Principal Authority

Australian Capital Territory

Environment Protection Act 1997 and regulations; Environmental Standards: Assessment & Classification of Liquid and Non-liquid Wastes (Environment ACT, 2000)

Environment ACT

New South Wales

Protection of the Environment Operations Act 1997 and regulations; Environmental Guidelines: Assessment, Classification and Management of Liquid and Non-Liquid Wastes (NSW EPA, 1999); Environmentally Hazardous Chemicals Act (1985); Chemical Control Order in Relation to Aluminium Smelter Wastes Containing Fluoride and/or Cyanide; Trade waste guidance (Sydney Water, 2000).

NSW Environment Protection Authority; Sydney Water Corporation

Queensland

Environment Protection Act (1994) and regulations; Environment Protection (Waste Management) Policy (2000) and Environmental Protection (Waste Management) Regulation (2000)

Queensland Environment Protection Agency

Northern Territory

Waste Management and Pollution Control Act 1998 and regulations; Water Supply and Sewerage Services Act and associated guidance: Acceptance Guidelines for Trade Waste (PAWA, 2000) and Trade Waste Code (PAWA, 2001).

Department of Infrastructure, Planning and Environment; Power and Water Authority

Western Australia

Environmental Protection Act (1986) and regulations (e.g. Environmental Protection (Controlled Waste) Regulations 2004, Environment Protection Regulation 1998); Mine Safety Inspection Act (1994). Mining Act (1978)

Department of Environment and Conservation;

Western Australian Environment Protection Authority; Department of Mineral and Energy



South Australia

Environment Protection Act (1993) and regulations; Sewer Act 1929

Department of Environment and Heritage, Environment Protection Agency

Victoria

Environment Protection Act (1970). Environment Protection (Prescribed Waste) regulations (1998); Industrial waste management policies

Victorian Environment Protection Authority

Tasmania

Environmental Management and Pollution Control Act (1994) and regulations; Plumbing Regulations (1994) (Trade Waste Standards)

Department of Primary Industries, Water and Environment


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