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 />
2.4.1 Assessment Endpoints<br />
Assessment endpoints, which represent key objectives for ecosystem protection at a site, are<br />
an expression of critical aspects of habitat structure and receptor viability that are important<br />
to protect (Suter, 1993; U. S. EPA, 1998). Assessment endpoints provide a transition between<br />
the ecological management goals and the measures used in the ERA. In addition, the<br />
identification of assessment endpoints serves to focus the ERA and reduce uncertainty,<br />
increasing the efficiency and cost-effectiveness of the risk assessment process. Assessment<br />
endpoints were initially identified in the Scoping Assessment (CH2M HILL, 1998b) and<br />
were revised based on new information gathered for the EEC Report and this ERA. These<br />
revised assessment endpoints were selected using four principal criteria: (1) their ecological<br />
relevance, (2) their political and societal relevance, (3) their susceptibility to known or<br />
potential stressors at the site, and (4) whether they represent the management goals for the<br />
site (U. S. EPA, 1998). The ecological management goals for the <strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong> are<br />
presented in Section 1.<br />
The assessment endpoints for the <strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong> are presented subsequently and in<br />
Table 2-21 with their associated measures:<br />
• Terrestrial and aquatic plants – Rates of growth, productivity, and survival; levels of<br />
abundance; species composition; and community structure capable of maintaining<br />
viable populations supportive of the post-proposed restoration community structures.<br />
• Terrestrial and aquatic invertebrates – Rates of growth and survival, levels of<br />
abundance, species composition, and community structure capable of maintaining<br />
viable populations supportive of the post-proposed restoration community structures.<br />
• Fish – Rates of species survival and reproduction and levels of abundance conducive to<br />
the maintenance of viable populations of individual species and supportive of the postproposed<br />
restoration community structures.<br />
• Migratory birds (species protected by the Migratory Bird Treaty Act) – Abiotic<br />
(sediment/soil and surface water) and biotic (prey populations) conditions favorable for<br />
health, survival, and reproduction of migratory birds.<br />
• Mammals – Rates of species survival and reproduction and levels of abundance<br />
conducive to the maintenance of viable species populations characteristic of expected<br />
post-proposed restoration community structures.<br />
• Individual special-status biota (including plants, fish, and wildlife that are considered<br />
threatened or endangered) – Rates of survival and reproduction necessary to maintain<br />
current populations and promote additional future recovery.<br />
2.4.2 Risk Hypotheses<br />
The risk hypotheses focus on the responses of the assessment endpoints when exposed to<br />
stressors and how the exposure could occur (U. S. EPA, 1998). The relationship between<br />
stressors and exposures was used in the Scoping Assessment (CH2M HILL, 1998b) to develop<br />
the risk hypotheses and ecological conceptual site models for the <strong>Bolsa</strong> <strong>Chica</strong> <strong>Lowlands</strong>.<br />
ERA REPORT 2-12 SAC/143368(002.DOC)<br />
7/31/02