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

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• determining estimated daily intake (EDI) <strong>of</strong> that chemical<br />

unrelated to any specific contaminated site (i.e. normal<br />

"background" exposure); <strong>and</strong><br />

• defining generic exposure scenarios appropriate to each l<strong>and</strong><br />

use.<br />

Soil guidelines must ensure that total exposure to a contaminant<br />

(EDI + on-site exposure at <strong>the</strong> guideline concentration) will<br />

present negligible risk.<br />

Some <strong>of</strong> <strong>the</strong> steps employed to derive human health soil<br />

remediation guidelines are similar to those used in a site-specific<br />

risk assessment. However, to establish <strong>the</strong>se generic guidelines,<br />

several basic assumptions were made about <strong>the</strong> sensitive receptor<br />

<strong>and</strong> <strong>the</strong> nature <strong>of</strong> chemical exposure <strong>for</strong> each l<strong>and</strong> use. Guidelines<br />

derived <strong>for</strong> non-carcinogens are based on an assumed threshold<br />

<strong>for</strong> toxic effects. For carcinogens presenting some risk at any level<br />

<strong>of</strong> exposure, guidelines are derived based on estimated lifetime<br />

incremental cancer risk from exposure to soil.<br />

Chemical constituents in soil can migrate <strong>and</strong> contaminate o<strong>the</strong>r<br />

media. For example, soil contaminants can:<br />

• leach into a groundwater drinking source;<br />

• migrate in a vapour phase into basements <strong>and</strong> contaminate<br />

indoor air;<br />

• be taken up by plants <strong>and</strong> garden produce.<br />

These important indirect <strong>and</strong> direct soil exposure pathways are<br />

considered in check mechanisms in this protocol. There are five<br />

checks but only two types <strong>of</strong> check mechanisms. The first check<br />

mechanism uses probabilistic analysis to determine generic input<br />

values <strong>for</strong> <strong>the</strong> model parameters. Both <strong>the</strong> groundwater <strong>and</strong><br />

volatilization into indoor air checks use this method, <strong>and</strong> <strong>the</strong><br />

results <strong>of</strong> <strong>the</strong> check may adjust <strong>the</strong> final soil quality guideline. The<br />

second check mechanism uses conservative models which may or<br />

may not adjust a guideline value (Management Adjustment<br />

Factors). The Subcommittee uses <strong>the</strong> term, Management<br />

Adjustment Factors, to acknowledge <strong>the</strong> necessarily imprecise<br />

nature <strong>of</strong> <strong>the</strong>se models, which use conservative point estimates,<br />

based on data <strong>and</strong> pr<strong>of</strong>essional judgement, <strong>for</strong> generic input<br />

values. Management Adjustment Factors are used in <strong>the</strong> check<br />

vi

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