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OVERVIEW OF THE IMPACT OF MINING ON THE ... - IIED pubs

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Mining methods vary widely and depend on the location, type and size of mineral resources. Surface mining<br />

methods are most economical in situations where mineral deposits occur close to the surface (e.g. coal, salts and<br />

other evaporite deposits or road quarry material) or form part of surface deposits (e.g. alluvial gold and diamonds,<br />

and heavy mineral sands). Typical surface mining methods include: strip mining and open pit mining, as well as<br />

dredge, placer and hydraulic mining in riverbeds, terraces and beaches. These activities always disrupt the<br />

surface and this, in turn, affects soils, surface water and near-surface ground water, fauna, flora and all alternative<br />

types of land-use (Fuggle & Rabie, 1996; Ashton, 1999).<br />

Shallow underground mining, up to about 50 metres below the surface, includes bord (room) and pillar mining<br />

(often used in coal mines), where pillars of the mineral seam are left to support overlying material. Many of the<br />

gold and copper mines in Zimbabwe, Zambia and the Democratic Republic of Congo are sited on historical<br />

workings that employed a variety of shallow underground mining techniques (Mendelsohn, 1961). In some of the<br />

older South African coalmines in the Witbank area, roof collapse has occurred after the mines were closed,<br />

allowing air to enter the old workings and promoting spontaneous combustion in the residual coal. Some of the<br />

abandoned workings in the Witbank area have continued to burn for many years and have resulted in unplanned<br />

surface collapse as well as ground and surface water contamination through acidification and salinization of local<br />

aquifers and streams (Wells et al., 1996; Fuggle & Rabie, 1996). Spontaneous combustion of exposed coal<br />

seams and stockpiles of coal fines is also experienced at the Hwange collieries in Zimbabwe and the Maamba<br />

Colliery in Zambia (SADC, 2001).<br />

A variety of deep underground mining techniques are required to extract ores located deep beneath the earth’s<br />

crust. Deep mining techniques include specialized ore extraction techniques, such as block caving and longwall<br />

mining, and require sophisticated infrastructure to ensure mine safety and maintain safe working environments.<br />

The principal environmental impacts associated with deep underground mining (for example, in gold, platinum,<br />

chrome and copper mines) are linked to the mine wastes and blasting residues brought to the surface by mine dewatering<br />

activities. These cause water pollution from leachates, as well as visual pollution, changes in land use,<br />

excessive dust, and surface subsidence as a result of mine dewatering activities.<br />

Offshore (sub-marine) mineral deposits such as diamonds, oil and gas, heavy mineral sands, phosphorite,<br />

glauconite and manganese occur off the shores of southern Africa and some of these are already exploited in<br />

various ways. These offshore mining activities differs according to the specific locality and the effects of the mining<br />

operation on intertidal, sub tidal or deep-sea marine environments (Gurney et al., 1996). Many offshore mining<br />

operations are vulnerable to inclement weather conditions that pose added risks of fuel and material spills and loss<br />

of human life (Ashton, 1999).<br />

Besides the rate and method of mining, the location, variety and scale of mine infrastructure also influences the<br />

nature and extent of impacts. Typical mine infrastructure includes: haul roads and ore dumps; ventilation shafts;<br />

surface facilities (e.g. offices, workshops, car parks and warehouses); tailings and waste rock disposal areas and<br />

methods; transport and service corridors (e.g. railway lines, roads, pipelines, conveyers, airstrips, port facilities,<br />

power, water and gas corridors); product stockpiles; ore processing facilities; chemicals and fuel storage and the<br />

locations of towns and housing facilities (Australian Environmental Protection Agency, 1995-1996; Fuggle & Rabie,<br />

1996; Ashton, 1999; Weaver & Caldwell, 1999).<br />

Each mineral ore reacts in distinct ways when brought to the surface and comes into contact with air and water,<br />

affecting or altering the type of impact that may be expected from the mining operation. Whilst many<br />

environmental impacts can be fairly severe, it is important to acknowledge that several sophisticated mitigation<br />

measures have been devised through the sharing of best practice approaches in the mining industry.<br />

2.3 Phases of mining and mineral processing operations<br />

The typical life cycle of a mining operation consists of a number of simultaneous or sequential phases and<br />

activities. For example: prospecting, development (including verification of the quantity and quality of ore and its<br />

amenability to various extraction and processing methods), construction, operation, staff housing and support,<br />

product stockpiling, mineral processing, waste management, rehabilitation and eventually, closure. The typical life<br />

span of a mine is in the region of 25 years although this can vary from less than 1 year to well over 100 years<br />

(Fuggle & Rabie, 1996).<br />

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