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Engineering Geology

Engineering Geology - geomuseu

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E n g i n e e r i n g G e o l o g y<br />

Table 8.5. Classification of landfill sites based on their hydrogeology (after Barber, 1982).<br />

With kind permission of the Water Research Council<br />

Designation Description Hydrogeology<br />

Fissured site, or site with Material with well- Rapid movement of leachate via<br />

rapid subsurface liquid developed secondary fissures, joints or through coarse<br />

flow permeability features sediments. Possibility of little<br />

dispersion in the groundwater or<br />

attenuation of pollutants<br />

Natural dilution,<br />

Permeable materials with Slow movement of leachate into<br />

dispersion and little or no significant the ground through an unsaturated<br />

attenuation of secondary permeability zone. Dispersion of leachate in the<br />

leachate<br />

groundwater; attenuation of<br />

pollutants (sorption,<br />

biodegradation, etc.) probable<br />

Containment of leachate Impermeable deposits Little vertical movement of<br />

such as clays or shales, leachate. Saturated conditions<br />

or sites lined with exist within the base of the landfill<br />

impermeable materials<br />

or membranes<br />

However, there is no guarantee that clay, soil cement, asphalt or plastic lining will<br />

permanently remain impermeable. Thus, the migration of materials from the landfill site into<br />

the substrata will occur eventually, although the length of time before this happens is subject<br />

to uncertainty. In some instances, the delay will be sufficiently long for the polluting potential<br />

of the leachate to be greatly diminished. One of the methods of tackling the problem of<br />

pollution associated with landfills is by dilution and dispersal of the leachate. Otherwise,<br />

leachate can be collected by internal drains within a landfill and conveyed away for treatment.<br />

Selection of a landfill site for a particular waste or a mixture of wastes involves a consideration<br />

of economic and social factors as well as the hydrogeological conditions. As far as the<br />

latter are concerned, most argillaceous sedimentary, massive igneous and metamorphic rock<br />

formations have low intrinsic permeability and therefore afford the most protection to water<br />

supply. In contrast, the least protection is provided by rocks intersected by open fissures or<br />

in which solution features are developed. Coarse-grained soils may act as filters leading to<br />

dilution and decontamination. Hence, sites for disposal of domestic refuse can be chosen<br />

where decontamination has the maximum chance of reaching completion and where groundwater<br />

sources are located far enough away to enable dilution to be effective. The position of<br />

the water table is important as it determines whether wet or dry tipping takes place, as is<br />

the thickness of unsaturated material underlying a potential site. Unless waste is inert, wet<br />

tipping should be avoided. The hydraulic gradient determines the direction and velocity of the<br />

flow of leachates when they reach the water table and is also related to both the dilution<br />

that the leachates undergo, and to the points at which flow is discharged. Gray et al. (1974)<br />

426

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