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 />

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

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

Saved successfully!

Ooh no, something went wrong!