16.05.2015 Views

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

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

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

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!