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 />
Stressors in the <strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong> consist of chemicals that have been released from<br />
their primary sources to the environment either directly from onsite activities or indirectly<br />
from offsite sources via stormwater runoff. Under current conditions, ecological receptors<br />
could contact contaminants in sediment/soil, surface water, and/or biota. Based on the<br />
chemical stressors and potential exposure routes, the risk hypotheses for the <strong>Bolsa</strong> <strong>Chica</strong><br />
<strong>Lowlands</strong> are:<br />
• Inorganic and organic chemicals associated with onsite activities are present at<br />
concentrations potentially toxic to terrestrial and aquatic plants, invertebrates, and<br />
vertebrates (birds, mammals, and fish).<br />
• Inorganic and organic chemicals associated with offsite sources are being conveyed onto<br />
the site and are present at concentrations potentially toxic to terrestrial and aquatic<br />
plants, invertebrates, and vertebrates (birds, mammals, and fish).<br />
• Chemicals associated with onsite and offsite source areas are potentially<br />
bioaccumulating in forage and prey species for secondary consumers, resulting in foodchain<br />
transfer of contaminants.<br />
Under current conditions in the <strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong>, ecological receptors could contact<br />
contaminants in sediment/soil, surface water, and biota. For example, terrestrial receptors<br />
might be exposed to the contaminants by direct contact with surface soils or sediments, or<br />
by incidentally ingesting them during activities such as feeding. Terrestrial and aquatic<br />
receptors could be exposed to contaminants in sediment/soil or surface waters at the site<br />
through direct contact or uptake of the water or sediment. If forage or prey species were<br />
contaminated from site-related chemicals, their consumers (herbivores, carnivores, or<br />
omnivores) might also become secondary receptors via food chain transfer.<br />
2.4.3 Measures<br />
Three categories of measures are predictive of the assessment endpoints (U.S. EPA, 1998):<br />
measures of exposure, measures of effect, and measures of ecosystem and receptor<br />
characteristics. Measures of exposure are used to evaluate how exposures could be occurring.<br />
Measures of effects are used to evaluate the response of the assessment endpoints when<br />
exposed to the stressor. Measures of ecosystem and receptor characteristics are used to<br />
evaluate the ecosystem characteristics that could affect exposure or response to the stressor.<br />
Measures identified for an ERA can be from one or more of these categories, depending on<br />
the complexity of the ERA. Criteria considered in the selection of measures are as follows:<br />
• Corresponds to or is predictive of an assessment endpoint<br />
• Can be readily measured or evaluated<br />
• Is appropriate to the scale of the site<br />
• Is appropriate to the temporal dynamics<br />
• Is appropriate to the exposure pathway<br />
• Is associated with low natural variability<br />
• Is minimally disruptive to ecological community and species variability<br />
SAC/143368(002.DOC) 2-13 ERA REPORT<br />
7/31/02