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536 CHAPTER 23 Materials Management<br />

Monitoring well<br />

above water table<br />

Monitoring well<br />

below water table<br />

Solid w<strong>as</strong>te<br />

Sand layer<br />

Compacted clay cap<br />

Compacted<br />

clay liner<br />

Pl<strong>as</strong>tic liner<br />

Water table<br />

Leachate<br />

collection pipe<br />

Groundwater flow<br />

(a)<br />

FIGURE 23.14 (a) Idealized diagram of a solid-w<strong>as</strong>te facility<br />

(sanitary landfill) illustrating multiple-barrier design, monitoring<br />

system, and leachate collection system. (b) Rock Creek landfill<br />

under construction in Calaver<strong>as</strong> County, California. This municipal<br />

solid-w<strong>as</strong>te landfill is underlain by a compacted clay liner,<br />

exposed in the center left portion of the photograph. The darker<br />

slopes, covered with gravel piles, overlie the compacted clay<br />

layer. These form a vapor barrier designed to keep moisture in<br />

the clay so it won’t crack. Trenches at the bottom of the landfill<br />

are lined with pl<strong>as</strong>tic and are part of the leachate collection system<br />

for the landfill. The landfill is also equipped with a system to<br />

monitor the water below the leachate collection system.<br />

(b)<br />

Landfills must have liners.<br />

Landfills must have a leachate collection system.<br />

Landfill operators must monitor groundwater for many<br />

specified toxic chemicals.<br />

Landfill operators must meet financial <strong>as</strong>surance criteria<br />

to ensure that monitoring continues for 30 years after<br />

the landfill is closed.<br />

EPA approval of a state’s landfill program allows<br />

greater flexibility:<br />

Groundwater monitoring may be suspended if the<br />

landfill operator can demonstrate that hazardous constituents<br />

are not migrating from the landfill.<br />

Alternative types of daily cover over the w<strong>as</strong>te may be used.<br />

Alternative groundwater-protection standards are<br />

allowed.<br />

Alternative schedules for documentation of groundwater<br />

monitoring are allowed.<br />

Under certain circumstances, landfills in wetlands and<br />

fault zones are allowed.<br />

Alternative financial <strong>as</strong>surance mechanisms are allowed.<br />

Given the added flexibility, it appears advantageous for<br />

states to develop EPA-approved w<strong>as</strong>te-management plans.<br />

Reducing the W<strong>as</strong>te<br />

that Ends Up in a Landfill<br />

Most of the municipal solid w<strong>as</strong>te we generate is from our<br />

homes, and over 50% of it could be diverted from the landfill<br />

by the 3 R’s of w<strong>as</strong>te management: reduce, reuse, and<br />

recycle. Diversion may eventually be incre<strong>as</strong>ed to <strong>as</strong> much<br />

<strong>as</strong> 85% through improved w<strong>as</strong>te management. In other<br />

words, the life of the landfill can be extended by keeping<br />

more w<strong>as</strong>te out of the landfill through conservation and<br />

recycling, or by turning w<strong>as</strong>te, even w<strong>as</strong>te that is presently<br />

buried, into a source of clean energy. The latter involves<br />

first removing materials that can be recycled, then linking<br />

noncombustion thermal or biochemical processes with the

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