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the flow of contaminants provides valuable alternatives for design and operation
of CDFs.
The HELPQ model predicts the concentration of contaminants in the CDF
and vadose (unsaturated) zone below the CDF. Concentrations are predicted in
the pore water and associated with the solid materials as a function of time.
Additionally, the model predicts the leachate flow rate and contaminant mass flux.
Saturated Zone Models. Modeling contaminant transport beyond the vadose
zone and to the receptor requires use of additional models such as the
MULTIMED model, the Multimedia Environmental Pollutant Assessment System
(MEPAS) (http://mepas.pnl.gov:2080/) or the Department of Defense
Groundwater Modeling System (GMS) (http://chl.wes.army.mil/software/gms/).
Similarly, for CDF sites where groundwater flows directly into the dredged
material (such as nearshore CDFs), more complex modeling operations using the
GMS may be needed to predict the movement and concentration of contaminants
at the CDF boundaries. Flow of anaerobic leachate through oxic dikes is another
complicated situation potentially requiring complex modeling to predict
contaminant concentrations.
6.4.5 Tier III Leachate Quality Decision
After consideration of the Tier III leachate quality information based on test
data and modeling, one of the following conclusions is reached (Figure 6-2):
1. Information is sufficient to reach a decision. In this case either:
a. Standards applicable to the intended use of the groundwater (Section
6.1.1) exist for all COC and are met for all COC after consideration
of attenuation. No further leachate evaluation is necessary.
b. Standards applicable to the intended use of the groundwater (Section
6.1.1) are exceeded for one or more COC after consideration of
attenuation, and management actions should be considered.
2. Information is not sufficient to reach a decision, which includes cases
where there are no standards applicable to the intended use of the
groundwater (Section 6.1.1). The case-specific risk from leachate should
be determined in Tier IV, or management actions as an alternative to
further evaluation should be considered. A decision to implement
management actions for leachate, such as design modification or leachate
collection, may require more detailed information prior to design of such
actions. If management actions are selected, no further leachate
evaluation is necessary.
6-15
Chapter 6
Leachate to Groundwater
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