Sanitary Landfills: Toward Sustainable Development - lumes
Sanitary Landfills: Toward Sustainable Development - lumes
Sanitary Landfills: Toward Sustainable Development - lumes
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LUMES 2000-2001<br />
<strong>Sanitary</strong> <strong>Landfills</strong>: <strong>Toward</strong> <strong>Sustainable</strong> <strong>Development</strong><br />
i) Base liner system that will contain leachate within landfill and prevent the leachate<br />
percolate through the landfill cell and contaminate the ground water<br />
ii) Leachate collection system that will remove the leachate<br />
iii) Leachate treatment system that will remove organic matter from the leachate<br />
iv) Daily soil covering to avoid flies and vectors breeding<br />
v) Final cover or top liner that will reduce infiltration and promote runoff<br />
vi) Diversion of surface runoffs around site to prevent water from filtering into the landfill<br />
vii) Gas venting to prevent and/or reduce landfill gases migration<br />
viii) Buffers at the boundary of the site<br />
ix) Internal drainage<br />
x) Proper access roads<br />
Liner design, in particular, should follow a set of rigour measures in order to prevent any possible<br />
leachate leakage and nearby surface water and groundwater contamination. Leachate collection<br />
and gas venting facilities are no less important in minimising the landfill environmental impacts.<br />
3.1.2.1 Lining and Capping<br />
In order to prevent leachate from polluting the surface water and ground water, there are two<br />
alternative landfill management strategies that can be adopted for leachate control:<br />
i) A site that is engineered to contain waste and leachate. The liner system consists of a<br />
composite base liner system of a soil and geo-membrane component overlaid by a geosynthetic<br />
leachate collection layer.<br />
ii) A site that allow leachate attenuated slowly by natural process. The liner system consists<br />
of a soil base and granular leachate collection system<br />
The composite base liner consists of an upper geomembrane liner and a lower compacted soil. In<br />
United States the minimum requirement for the geomembrane is at least 30mm thick, and if a<br />
high density of polytheylene (HDPE) geomembrane is used, the minimum thickness required is<br />
60mm. The compacted soil liner must be at least 60cm in thickness and with a hydraulic<br />
conductivity of less than 1 x 10 -7 cm per second (USEPA, 1994). But as concerned by Allen<br />
(2001), the lifespan of the landfill liner is yet to be sure and there is a high probability that the<br />
leachate could form and leach through the artificial liner as the liner deteriorates along time and<br />
the interaction with the chemical components in the landfill cell. He suggested that the landfill<br />
should be situated at land with natural hydrogeological characteristics which can contain and<br />
naturally attenuate contaminants to acceptable level instead of trying to contain the contaminants<br />
within the landfill by relying on artificial liners.<br />
A final cover or cap is important in landfill design too. It should be designed in a way that can<br />
reduce infiltration and promote runoff and evaporation. In order to do so, a low permeable or<br />
impermeable liner will be laid on top of the waste. Runoff control is essential because it can carry<br />
leachate near the surface of the landfill to nearby surface water sources, such as streams or rivers<br />
and cause contamination.<br />
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