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Wambo Coal AEMR 2011-2012 - Peabody Energy

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<strong>2011</strong>-<strong>2012</strong> <strong>AEMR</strong><br />

3.3 Erosion & Sediment<br />

Control<br />

3.3.1 Environmental Management<br />

Erosion and sedimentation is managed in<br />

accordance with WCPL Erosion and Sediment<br />

Control Plan (ESCP), a requirement of Consent<br />

Condition 32, Schedule 4 of DA305-7-2003. The<br />

ESCP is a component of WCPL’s Site Water<br />

Management Plan as required under Condition 30,<br />

Schedule 4 of DA305-7-2003. The main principles<br />

of the ESCP include:<br />

Separation of runoff from disturbed and<br />

undisturbed areas where practicable;<br />

Construction of sediment structures or<br />

utilisation of existing mine water storages to<br />

capture runoff up to a specified design criterion;<br />

<br />

<br />

Construction of surface drains to facilitate the<br />

efficient transport of surface runoff. Drains are<br />

designed using trapezoidal or parabolic crosssections;<br />

and<br />

Progressive rehabilitation stabilisation of mine<br />

infrastructure areas.<br />

These principles take into account the general<br />

recommendations for site drainage works presented<br />

in “Managing Urban Stormwater – Soils and<br />

Construction Volume 1” (Landcom 2004).<br />

<br />

<br />

<br />

<br />

The use of a street sweeper to remove dirt and<br />

mud from mine access roads;<br />

Monthly monitoring of all sediment control<br />

structures and maintenance when required;<br />

Limiting clearance and disturbance of the<br />

natural environment; and<br />

Progressive rehabilitation across site.<br />

3.3.2 Environmental Performance<br />

Monthly inspections of sediment control structures<br />

as well as inspections following rainfall events of 20<br />

mm or more in a 24 hour period are conducted<br />

across the mine by WCPL personnel and<br />

contractors. During these inspections, sediment<br />

control structures are inspected for capacity,<br />

structural integrity and effectiveness.<br />

The routine removal of sediment from a number of<br />

the sediment control structures, including Hales<br />

Crossing Sediment Dam was undertaken during the<br />

reporting period. As discussed in the last <strong>AEMR</strong>, a<br />

plan of works to remove coal sediment from a series<br />

of purpose built sediment dams around the CHPP<br />

and product stockpile areas was scheduled for<br />

<strong>2011</strong>. Dredging to remove coal fines and increase<br />

the dam capacity within the Gordon Below Franklin<br />

Dam commenced in June <strong>2011</strong>. The recovered coal<br />

fines were reprocessed through the CHPP.<br />

A number of strategies are used on site for erosion<br />

and sediment control including:<br />

<br />

The establishment of diversion banks on the<br />

upstream side of the site to divert clean water<br />

around the site and into natural drainage lines;<br />

The establishment of catch drains in<br />

accordance with relevant criteria (outlined in the<br />

ESCP) to direct sediment-laden water into<br />

sediment control structures;<br />

The strategic placement and design of<br />

sediment control structures on site to treat<br />

sediment laden water before it leaves site;<br />

<br />

<br />

<br />

The placement of hay bales along catch drains<br />

to control the velocity of flow and prevent<br />

scouring;<br />

The establishment of sediment ponds or<br />

utilisation of existing mine water structures to<br />

treat sediment laden water;<br />

The establishment of sediment fencing as<br />

required on the down-slope side of soil<br />

stockpiles;<br />

Dredging Eagles Nest Dam in June <strong>2012</strong><br />

During the reporting period WCPL commenced<br />

rehabilitation program within the NWC Diversion<br />

Stage 3. Please refer to Section 5.1.4 for further<br />

details about the NWC Diversion rehabilitation<br />

works.<br />

Page 48

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