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1.1 MB pdf - Bolsa Chica Lowlands Restoration Project

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SECTION 2: PROBLEM FORMULATION<br />

Numerous clean-up actions have occurred over the past two decades. While no formal<br />

remediation was performed when the State Ecological Reserve was created and partially<br />

diked (1977 to 1978), visibly contaminated soils and debris were scraped off the Reserve<br />

areas and removed. Cleaner, but probably untested, in situ soils were used to build the<br />

dikes around the Reserve.<br />

Extensive remediation associated with the active oil field “waste handling facility” was<br />

carried out in the 1980s and 1990s. More recently CalResources, now AERA Energy, working<br />

with Signal Landmark/Koll, has remediated decommissioned oil wells, pipelines, and oil<br />

field facilities, such as the former tank farms and gas plant, as well as accidental spills.<br />

Under the terms of the site purchase and proposed habitat restoration agreement<br />

(Memorandum of Agreement, October 1996, Amended December 1996 and February 1997),<br />

portions of the <strong>Lowlands</strong> will continue to be operated by AERA Energy as an active oilfield.<br />

If sufficient funds are available to buy out producing wells or as the wells are phased out,<br />

closed down, and cleaned up, these active oilfield areas will also be restored fully to coastal<br />

wetland habitats.<br />

2.2 Ecological Characterization<br />

<strong>Bolsa</strong> <strong>Chica</strong> is classified as a bay estuary having deepwater habitats with extensive intertidal<br />

wetlands (Ferren, 1990; OCEMA, 1996). The <strong>Bolsa</strong> <strong>Chica</strong> Wetlands are the remnant of what<br />

was once a vast saltwater and freshwater wetlands complex in the historic floodplain of the<br />

Santa Ana River. The generally open and broad mouth of the bay allowed marine water to<br />

flood the adjacent marshes at low elevation during high tide. During the winter wet season,<br />

rainfall and streamflow dilute the marine waters; during the rest of the year, ocean water<br />

dominates.<br />

2.2.1 Identification of Habitats<br />

The <strong>Lowlands</strong> include habitats that at one time supported salt marsh, brackish marsh,<br />

freshwater marsh, open water, mudflats, dunes, and sandy flats. The present condition of<br />

these lowland habitats has been altered and degraded by development that has removed<br />

much of the site from tidal influence. These alterations include dike construction, road and<br />

pad construction for oil development, and channel construction for flood control. Removal<br />

from tidal influence has adversely affected much of the salt marsh habitat, which is now<br />

mostly degraded or ruderal habitat (i.e., weedy species tolerant of poor soils, including<br />

mustard, ice plant, and telegraph weed).<br />

Habitat types found in the <strong>Lowlands</strong> are briefly described in text and are shown on Figure 2-4.<br />

2.2.<strong>1.1</strong> Pickleweed<br />

Saline tidal and non-tidal areas with adequate soil moisture are dominated by pickleweed<br />

(Salicornia virginica). Other species associated with the pickleweed salt marsh habitat include<br />

alkali heath (Frankenia salina), saltgrass (Distichlis spicata), and annual pickleweed (Salicornia<br />

bigelovii). In non-tidal areas, ice plant (Carpobrotus edulis) is often co-dominant.<br />

SAC/143368(002.DOC) 2-5 ERA REPORT<br />

7/31/02

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