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2008 Annual Monitoring Report (pdf 10.9MB) - Bolsa Chica ...

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<strong>Bolsa</strong> <strong>Chica</strong> Lowlands Restoration <strong>Monitoring</strong><br />

<strong>2008</strong> <strong>Annual</strong> <strong>Report</strong><br />

Discussion<br />

Considerable variability in the infaunal invertebrate community was recorded by the coring work.<br />

Patchiness is an established characteristic of benthic invertebrate communities. Most marine<br />

invertebrates are rapid colonizers, with community composition being driven by sediment<br />

characteristics and the frequency and spatial scale of disturbances (Thrush et al. 1996, Levin and<br />

Talley 2002). The variability see in invertebrate abundance and biomass through time and across<br />

stations in <strong>2008</strong> can be attributed to an uneven distribution of food or other resources, subtle substrate<br />

differences, or localized environmental impacts within a community. During the sediment core<br />

collection, considerable variability in sediment type was noted within stations, with some having a<br />

hard clay component, others with clean sand, and others composed of very soft muds. Additionally,<br />

the monitoring program was not conducted at a frequency capable of identifying seasonal patterns or<br />

with enough replication to detect directional trends amidst the high variability within station<br />

elevations.<br />

However, the two sampling events during the second year post-restoration did serve to document that<br />

the creation of the FTB has provided benthic food resources available to birds, fish, and other<br />

invertebrates. The created basin was quickly colonized by polychaetes, amphipods, tanaids, bivalves,<br />

and gastropods. Similar trends were seen at Batiquitos Lagoon following the introduction of marine<br />

influence to the wetland, which was quickly dominated in both density and biomass by molluscs<br />

(gastropods and bivalves), annelids (primarily polychaetes), and arthropods (primarily crustaceans)<br />

(M&A 2009). Benthic monitoring conducted during the comparable second year post-restoration at<br />

Batiquitos Lagoon (1998) found the mean density of all infauna at the –2-foot elevation to be 3,518<br />

indiv./m 2 in January and 3,020 indiv./m 2 in July, and at the +1-foot elevation to be 2,265 indiv./m 2 in<br />

January and 2,321 indiv./m 2 in July (Merkel & Associates 2009). The mean densities found at <strong>Bolsa</strong><br />

<strong>Chica</strong> in <strong>2008</strong> were within the same order of magnitude, with a density at the –2-foot elevation of<br />

6,365 indiv./m 2 in January and 3,540 indiv./m 2 in July, and at the +1-foot elevation a mean density of<br />

2,172 indiv./m 2 in January and 8,562 indiv./m 2 in July. This suggests infaunal density is not falling<br />

short after the second year post-restoration.<br />

The FTB experienced considerable tidal muting during the first two years post-restoration, with its<br />

ability to drain at low tides increasingly hampered over time by the accumulation of the anticipated<br />

sand shoal in the inlet (see Appendix 2-A). This had the effect of increasing the inundation period at a<br />

given elevation, so that by the end of <strong>2008</strong>, the +1-foot elevation was exposed much less frequently at<br />

low tides. This inundation shift probably had an effect on the invertebrate community that could not<br />

be detected by the limited sampling program, but likely influenced the distribution of fauna<br />

elevationally. Following maintenance dredging scheduled for 2009, the tidal range will rapidly be<br />

restored and subject the infaunal community to a less gradual shift in tidal elevation. The benthic<br />

community is anticipated to respond quickly, re-establishing at the elevations with the appropriate<br />

inundation conditions for their environmental tolerances. Although the response of the benthic<br />

community to tidal muting is not monitored, it should additionally be kept in mind when considering<br />

the variability between stations and seasons.<br />

The lack of lower level taxonomic data makes it impossible to compare the relative health of the FTB<br />

benthic communities with some popular indices (e.g., Index of Biotic Integrity, Benthic Response<br />

Index) to local reference standards. However, the basic goal of the sampling program was met;<br />

monitoring allowed documentation of the conversion of the basin to a tidally influenced bay capable of<br />

supporting a substantial prey base of infauna for marine fish and birds present in the basin.<br />

Merkel & Associates, Inc. 65

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