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Mine Rehabilitation Handbook - Mining and Blasting

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C. When using jute mesh<br />

PLACE MESH OVER<br />

SEEDED AND FERTILISED<br />

TOPSOIL. BURY THE TOP<br />

END OF THE JUTE MESH<br />

STRIP IN A TRENCH<br />

150mm IN DEPTH<br />

LAY MESH AND ENSURE<br />

CONTACT WITH SOIL AT<br />

ALL TIMES<br />

Figure 5.6<br />

• Encouraging Infiltration<br />

This is often, but not always, most effectively achieved by ripping the<br />

disturbed area parallel to the contours. In addition to increasing<br />

infiltration, ripping relieves soil compaction, “keys” topsoil to subsoil,<br />

increases the volume of soil readily available to plant roots <strong>and</strong><br />

provides places for seeds to lodge. Important considerations when<br />

ripping include:<br />

- always rip precisely along the contour - this will normally require a<br />

surveyed line;<br />

- rip the area following development of the post mining l<strong>and</strong> form;<br />

- ripping should normally be as deep as possible 0.8 - 1.8m<br />

depending on the material, available equipment <strong>and</strong> subsurface<br />

conditions;<br />

- spacing of rip-lines should be approximately equal to ripping depth;<br />

- do not rip when soil conditions are too wet to allow the soil<br />

to shatter;<br />

- a “winged” ripping line may be more effective in moist<br />

soil conditions;<br />

- take care when ripping sodic materials, as they are prone to tunnel<br />

erosion (piping); <strong>and</strong><br />

- avoid drawing large rocks to the surface whilst ripping.<br />

27<br />

SECURE MESH WITH<br />

U-SHAPED WIRE STAPLES<br />

• Managing Water Leaving the Site<br />

Water, which is discharged from the site, or is diverted away from the<br />

site, will generally have been controlled <strong>and</strong> the flow concentrated.<br />

Diversion of established drainage lines or watercourses would<br />

normally require specific approval from the State/Territory water<br />

authority. Similarly, diversion or discharge of runoff may have legal<br />

implications <strong>and</strong> necessary approval or permits should be obtained.<br />

Unless the water can be utilised by the mining operation, it must be<br />

managed to avoid pollution due to erosion <strong>and</strong> sediment deposition,<br />

either at the point of discharge or further downstream. As a guide:<br />

- Sediment dams are most commonly used to control <strong>and</strong> retain<br />

sediment laden runoff prior to discharge.<br />

- Most sediment will be carried by the infrequent high intensity<br />

rainfall events. Dams <strong>and</strong> spillways must be designed to<br />

accommodate these events or they will not function at the most<br />

critical times. Seek advice from appropriate authorities or detailed<br />

references for design techniques (refer Appendices 1 & 3).<br />

- Ensure that construction materials are suitable. Leakage from the<br />

dam may in itself not be critical but consequent instability of the<br />

dam wall due to tunnel erosion (piping) may result in failure.<br />

- Locate dams so that runoff from undisturbed catchments can be<br />

diverted to natural waterways. Ensure that channel gradients are<br />

not excessive <strong>and</strong> the need for protective measures within the<br />

channel is minimised.<br />

- In many dams, sediment levels greater than half of the total dam<br />

capacity will significantly reduce sediment removal rated. In these<br />

circumstances, sediment should be removed (refer figure 5.7).<br />

- In saline areas, be aware that the head (pressure) of a dam on a<br />

slope may cause salt scalding downslope of the dam.<br />

Figure 5.7<br />

28

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