1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
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SECTION 2: PROBLEM FORMULATION<br />
2.5.2 Exposure Pathway Inclusion/Exclusion<br />
The exposure pathway inclusion/exclusion evaluation is based on information gathered<br />
from the problem formulation (Sections 2.2, 2.3, and 2.4) and the selection of representative<br />
species, the probable completeness of each exposure pathway, and the potential for that<br />
pathway to be a major or minor route of exposure and risk.<br />
A complete exposure pathway must exist for an exposure to occur. A complete exposure<br />
pathway must have the following elements, in addition to the presence of suitable habitat<br />
for ecological receptors:<br />
• Contaminant source (e.g., chemicals in waste sumps, etc.)<br />
• Mechanism for contaminant release and transport (e.g., surface dispersion)<br />
• Exposure point (e.g., wetland Cell, creek, or soil)<br />
• Feasible route of exposure (e.g., ingestion)<br />
• Receptor (e.g., fish, bird, or mammal)<br />
Contaminant sources and release mechanisms in the <strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong> consist primarily<br />
of onsite source areas (waste sumps, pipelines, and maintenance areas) and runoff/surface<br />
dispersion of chemicals from the onsite areas or from offsite sources (such as urban runoff).<br />
Ecological receptors can be exposed to chemicals in soil, sediment, or surface water via direct<br />
or secondary exposure pathways. Direct exposure pathways include ingestion, dermal<br />
contact, root update, uptake/transport access gills, and potentially the inhalation of organic<br />
vapors or soil particulates. Secondary exposure pathways are limited to food-chain transfer<br />
of chemicals that bioaccumulate. Potential exposure pathways for representative species are<br />
summarized in Table 2-23 along with the rationale for inclusion/exclusion in the quantitative<br />
and qualitative evaluations to be conducted in the ERA.<br />
Terrestrial and aquatic plants can absorb chemicals via root uptake from sediment/soil or<br />
surface water. Many chemicals absorbed by plants are deposited in the leaves. In addition to<br />
direct toxicity to the plant, chemicals that bioaccumulate within plant tissues (e.g., leaves)<br />
may result in food chain transfer of chemicals to higher trophic-level organisms.<br />
Terrestrial and aquatic invertebrates can absorb chemicals through their epidermis and can<br />
accidentally or purposefully ingest sediment during feeding or burrowing. Benthic<br />
organisms are especially prone to exposure to chemicals in sediments as some consume the<br />
organic materials from within the sediment (e.g., chironomids). Aquatic invertebrates also<br />
serve as a major route of food chain transfer, because they are prey for other aquatic<br />
organisms (e.g., fish) and semi-aquatic wildlife (e.g., shorebirds).<br />
Terrestrial and semi-aquatic birds (e.g., shorebirds) and terrestrial mammals can be exposed<br />
to chemicals in sediment/soil or surface water from several different behaviors. Animals<br />
can inadvertently or purposefully ingest sediment/soil while grooming, burrowing, or<br />
consuming contaminated prey species. Surface water can be ingested as a drinking water<br />
source or during bathing or grooming activities. Dermal contact with sediment/soil or<br />
surface water is considered a secondary route of exposure for birds and mammals. Dermal<br />
contact is of concern primarily with organic chemicals that are lipophilic (i.e., have an<br />
affinity for fats) and can cross the epidermis of the exposed organism. Although some of the<br />
COPECs (e.g., DDT ) are highly lipophilic and can bioaccumulate, they are of greater<br />
concern in the food chain pathway as opposed to direct contact.<br />
SAC/143368(002.DOC) 2-17 ERA REPORT<br />
7/31/02