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Protocol for the Derivation of Environmental and Human ... - CCME

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Appendix D<br />

<strong>Derivation</strong> <strong>of</strong> Dilution Factor <strong>for</strong> Recharge Water in<br />

Groundwater<br />

1.0 Guiding Assumptions <strong>and</strong> Rationale<br />

Equilibrium partitioning concepts predict <strong>the</strong> concentration <strong>of</strong> a non-polar organic chemical in water<br />

draining from a soil at a contaminated site (See Appendix C). Estimating <strong>the</strong> effect <strong>of</strong> this recharge on<br />

groundwater quality requires that dilution be considered. Several assumptions are made to allow a<br />

generic treatment <strong>of</strong> <strong>the</strong> dilution problem:<br />

1. Site is underlain by an unconfined aquifer.<br />

Rationale: This is a fairly common arrangement <strong>and</strong> is among <strong>the</strong> most sensitive. O<strong>the</strong>r<br />

stratigraphic arrangements that commonly occur should also be protected if<br />

guidelines are developed under <strong>the</strong> unconfined aquifer assumption.<br />

2. Entire site has been remediated to <strong>the</strong> preliminary soil quality guideline concentration.<br />

Rationale: Residual contamination may be found in hotspots or throughout a site. However, a<br />

generic approach to groundwater protection must address <strong>the</strong> more severe<br />

condition.<br />

3. Groundwater <strong>for</strong> drinking is or could be withdrawn from a well located along <strong>the</strong> down gradient<br />

boundary <strong>of</strong> <strong>the</strong> remediated site.<br />

Rationale: A general objective <strong>for</strong> remediation guidelines is that <strong>the</strong>y will not result in <strong>of</strong>f-site<br />

movement beyond relevant generic guidelines. This is compatible with regulations in<br />

most Canadian jurisdictions.<br />

4. Compliance with objectives set under assumption three is required now <strong>and</strong> in <strong>the</strong> future.<br />

Rationale: If groundwater is to be protected <strong>for</strong> drinking, a generic remediation exercise must be<br />

effective at <strong>the</strong> time <strong>of</strong> completion — i.e., management <strong>of</strong> contamination plumes that<br />

would render <strong>the</strong> water unpotable <strong>for</strong> any period <strong>of</strong> time would normally be<br />

conducted under risk assessment procedures.<br />

5. Soil organic matter in <strong>the</strong> zone <strong>of</strong> contamination is <strong>the</strong> principal attenuating factor.<br />

Rationale: Soil conditions presented in <strong>the</strong> protocol ensure that in <strong>the</strong> zone <strong>of</strong> contamination<br />

organic matter should prevail over o<strong>the</strong>r sorbent properties. It is also assumed that<br />

significant sinks <strong>for</strong> contamination do not exist between <strong>the</strong> aquifer <strong>and</strong> <strong>the</strong><br />

contaminated zone. If significant attenuation is expected by virtue <strong>of</strong> buried,<br />

143

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