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