EIA-REP-325d-12 _BB_ - 201.09.14.pdf - SAHRA
EIA-REP-325d-12 _BB_ - 201.09.14.pdf - SAHRA
EIA-REP-325d-12 _BB_ - 201.09.14.pdf - SAHRA
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Source of impact<br />
Seepage from the stockpiles and AMD from mining operations causes a contamination plume affecting the<br />
underground resources which in turn affects surface water resources. Contamination may also occur directly into<br />
surface watercourses.<br />
Hydrocarbon-based fuels or lubricants spilled from construction vehicles.<br />
Description of the impacts<br />
Surface mining generally removes 90% or more of the coal (which often contains the highest sulphide content<br />
and hence the acid-producing potential) thereby leaving little in the backfill for continued reaction and acid<br />
generation. Pyrite is often dispersed among other rocks above and below the coal seam. The pyrite-bearing<br />
rocks and coal left behind are broken apart by blasting giving high surface area, and the acid products are<br />
leached fairly rapidly, typically within 10 to 20 years (Demchak et al, 2004). Carbonate rocks within the<br />
overburden may neutralise some or all of the AMD generated during surface mining. Special handling of toxic<br />
materials may reduce the amount of pyrite oxidized, and the addition of alkaline material during mining may<br />
neutralize acid in situ, both of which decrease the total acid load coming from the site (Demchak et al, 2004).<br />
During the ensuing 20 yr after reclamation, discharge water quality may reach pre-mining levels.<br />
Hydrocarbon-based fuels or lubricants spilled from construction vehicles, construction materials that are not<br />
properly stockpiled and litter deposited by construction workers may also be washed into the surface water<br />
bodies. Should appropriate toilet facilities not be provided for construction workers at the construction crew<br />
camps, the potential exists for surface water resources and surroundings to be contaminated by raw sewage.<br />
The utilisation of the water courses for disposal of water used for washing will decrease the abundance and<br />
diversity of aquatic macroinvertebrates inhabiting wetlands associated with the proposed development and<br />
further downstream. Contaminated runoff from concrete mixing and sediment release including hydrocarbon<br />
spillages may lead to the infiltration of toxicants into the groundwater.<br />
Significance:<br />
The significance is assessed to be medium high.<br />
Mitigation:<br />
• To assess the impacts of the stockpile area on the groundwater regime a groundwater analysis need to<br />
be undertaken;<br />
• A contaminant plume after 5, 10, 15, years should be modeled. Contaminated groundwater from the<br />
stockpile area will migrate and this assessment need to determine the direction and propose possible<br />
mitigation measures;<br />
• The contaminant plume could result in an impact on downstream water bodies, aquatic ecosystems and<br />
surrounding landowners, especially in the long term (more than 50 years);<br />
• Disposal of coal stockpile on natural clay;<br />
• Management of the stockpile in accordance with Section 73 of the MPRDA Regulations (No. R527,<br />
2004).<br />
• Vehicles are to be maintained in good working order so as to reduce the probability of leakage of fuels<br />
and lubricants.<br />
<strong>EIA</strong>-<strong>REP</strong>-<strong>325d</strong>-11<br />
October 20<strong>12</strong><br />
<strong>12</strong>4