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

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Part B, Section 5<br />

grazing herbivore soil <strong>and</strong> food ingestion exposures on agricultural l<strong>and</strong>s <strong>for</strong> guidelines derivation. These<br />

pathways also pertain to herbivorous wildlife that may graze on agricultural l<strong>and</strong>s (Beyer et al., 1992).<br />

Dermal contact by livestock <strong>and</strong> wildlife (resident <strong>and</strong> transitory) with contaminated soil may pose a<br />

significant health risk to <strong>the</strong>se organisms. In spite <strong>of</strong> this, in<strong>for</strong>mation on <strong>the</strong> effects from dermal contact<br />

with contaminated soil by livestock <strong>and</strong> wildlife is severely lacking (OECD, 1988). Because <strong>of</strong> <strong>the</strong>se<br />

data limitations, it is assumed that <strong>the</strong> level <strong>of</strong> protection <strong>of</strong>fered to soil-dependent organisms from<br />

dermal exposure is adequate to protect livestock <strong>and</strong> wildlife from <strong>the</strong> same exposure. This assumption<br />

is based on <strong>the</strong> notion that soil-dependent organisms are more directly in contact with <strong>the</strong> medium <strong>for</strong> a<br />

large portion <strong>of</strong> <strong>the</strong>ir life-cycle, <strong>and</strong> will experience adverse effects sooner than most organisms at higher<br />

trophic levels. This assumption will be held except where explicit in<strong>for</strong>mation to <strong>the</strong> contrary exists.<br />

However, effects from dermal contact should be considered <strong>for</strong> guidelines derivation when in<strong>for</strong>mation<br />

becomes available.<br />

5.2 Residential/Parkl<strong>and</strong> L<strong>and</strong> Use<br />

The combination <strong>of</strong> different activities under one l<strong>and</strong> use category can complicate <strong>the</strong> decision <strong>of</strong> which<br />

key receptors should be evaluated in an exposure scenario <strong>for</strong> residential/parkl<strong>and</strong> l<strong>and</strong> use. However,<br />

a common requirement among <strong>the</strong>se l<strong>and</strong> uses is to provide l<strong>and</strong>scape <strong>and</strong> ecological settings that<br />

support <strong>the</strong> main l<strong>and</strong> use activities (e.g., residential <strong>and</strong> parkl<strong>and</strong> l<strong>and</strong>scaping). Similar to agricultural<br />

l<strong>and</strong> use, <strong>the</strong> development <strong>of</strong> soil quality guidelines <strong>for</strong> residential/parkl<strong>and</strong> l<strong>and</strong> use must ensure that <strong>the</strong><br />

soil is capable <strong>of</strong> sustaining soil-dependent species <strong>and</strong> does not adversely affect wildlife from dermal<br />

contact <strong>and</strong> ingestion <strong>of</strong> contaminated soil or food. A generic exposure scenario <strong>for</strong> <strong>the</strong><br />

residential/parkl<strong>and</strong> l<strong>and</strong> use category reflecting exposure pathways <strong>and</strong> receptors <strong>of</strong> choice is illustrated<br />

in Figure 6.<br />

5.2.1 Growth <strong>of</strong> Ornamental <strong>and</strong> Native Flora<br />

To ensure that residential/parkl<strong>and</strong> l<strong>and</strong> use can support both ornamental <strong>and</strong> native flora, soildependent<br />

biota (whose ecological function helps sustain plant growth) must be protected from adverse<br />

effects as a result <strong>of</strong> dermal contact with contaminated soil (see Figure 6). Dermal contact by plant<br />

roots <strong>and</strong> seeds must also be examined. Root uptake <strong>and</strong> accumulation <strong>of</strong> contaminants will be<br />

examined as it relates to <strong>the</strong> ingestion <strong>of</strong> plant matter by wildlife.<br />

Sufficient toxicological in<strong>for</strong>mation exists to consider dermal soil contact by microbes (<strong>and</strong> <strong>the</strong>ir effect<br />

on nutrient cycling), soil invertebrates (e.g., decomposers), <strong>and</strong> crops <strong>and</strong> plants (e.g., seeds <strong>and</strong> roots)<br />

<strong>for</strong> guidelines derivation <strong>for</strong> <strong>the</strong> protection <strong>of</strong> ornamental <strong>and</strong> native plant growth (Figure 6). Currently,<br />

<strong>the</strong>re is insufficient in<strong>for</strong>mation to incorporate dermal absorption <strong>and</strong> translocation <strong>of</strong> contaminants by<br />

crops <strong>and</strong> plants via aerial deposition into generic guidelines derivation, but <strong>the</strong>se exposure pathways<br />

should be examined when in<strong>for</strong>mation becomes available.<br />

35

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