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of leachate exposed to a receptor (such as a well ) is further impacted by disperion
or mixing as the leachate is transported from the CDF locale to the receptor
through the coarse-grained layers of an aquifer. In effect, the contaminant
concentration in the leachate is diluted by the groundwater flow. Attenuation by
adsorption to organic matter and interactions with fine-grained materials will also
occur in the aquifer, but the effect is generally small as a result of low
concentration of organic and clayey materials in the main regions of saturated
groundwater flow.
Figure 6-2. Illustration of the vadose zone, saturated groundwater flow zone, and leachate pathway to
groundwater receptors
Leachate generation and transport depend on site-specific hydrology,
engineering controls at the disposal site, dredged material hydraulic conductivity,
initial water content, and nature of contaminants. Therefore, evaluation of
potential leachate impacts will be greatly affected by the nature of the site and the
engineering controls in place. Varying the engineering controls during the
evaluation also allows selection of the optimum controls.
Two aspects of leachate generation from CDFs are of particular concern:
1. Leachate contaminant concentrations. If maximum leachate
contaminant concentrations do not exceed applicable groundwater
standards, this may be sufficient to indicate no need for leachate
management actions. However, maximum leachate concentrations
exceeding such standards, without consideration of leachate flow and
dispersion, do not provide sufficient basis for a decision to implement
leachate control measures.
2. Leachate flow. The flow of leachate from the CDF and its interaction
with groundwater flow is the mechanism for migration to a receptor. The
most significant effect of a CDF leachate management action is in the
leachate mass flow. For example, mass flow through a 1-m lift of the
same dredged material will be higher from a 2-ha site than from a 1-ha
site with the same precipitation and climate. Leachate concentrations at
6-3
Chapter 6
Leachate to Groundwater
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