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appendix b final 2008 biological surveys of los angeles and long ...

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7.0 Kelp <strong>and</strong> Macroalgae<br />

Overall, outer harbor transects were dominated by Macrocystis <strong>and</strong> Egregia (Table 7.4-1).<br />

Macrocystis was present at all outer harbor sites, but was not observed a<strong>long</strong> any inner harbor<br />

transects. Egregia, a shallow subtidal to intertidal alga, was present at eight <strong>of</strong> twelve outer<br />

harbor sites. This species generally occupied relatively shallow water habitats while<br />

Macrocystis was found in slightly deeper waters. Understory species such as the coralline red<br />

algae Corallina spp. <strong>and</strong> the brown algae Dictyota <strong>and</strong> Colpomenia were also common in outer<br />

harbor habitats (Table 7.4-1). The invasive brown algae Sargassum muticum <strong>and</strong> Undaria were<br />

found at ten <strong>of</strong> the twelve <strong>and</strong> seven <strong>of</strong> twelve outer harbor sites, respectively (see Section 7.6).<br />

7.5 HISTORICAL COMPARISONS<br />

Giant kelp, Macrocystis pyrifera, has a relatively short history within the Ports <strong>of</strong> Los Angeles<br />

<strong>and</strong> Long Beach. Port habitats supported little Macrocystis until transplantation efforts in 1977<br />

(Rice 1983). Spatial distribution data for Macrocystis in the Ports prior to the 2000 baseline<br />

study is limited. Some kelp surface canopy coverage data is available from aerial <strong>surveys</strong><br />

performed in 1989 by the California Department <strong>of</strong> Fish <strong>and</strong> Game (CDFG), but the data set is<br />

limited to small areas adjacent to the outer breakwater. MEC (1988) studied the fauna <strong>of</strong> the<br />

kelp forest a<strong>long</strong> the breakwater near the current station T2, but did not map kelp elsewhere in<br />

the harbor complex. Anecdotal data suggests that kelp abundance in the Ports has increased<br />

significantly since 1977 <strong>and</strong> that relative densities have fluctuated in t<strong>and</strong>em with coastal<br />

populations at Pa<strong>los</strong> Verdes (MEC 1988). Regional kelp abundance has only recently started to<br />

recover from significant die <strong>of</strong>fs attributed to El Niño events in the 1980s <strong>and</strong> 1990s.<br />

Comparisons <strong>of</strong> CDFG aerial <strong>surveys</strong> performed throughout California in1989, 1999, <strong>and</strong> 2002-<br />

2006 found a noticeable increase in kelp surface canopy coverage within the Southern<br />

California Bight during recent years.<br />

Increases in giant kelp density are also due to increases in available habitat in the outer harbors<br />

<strong>of</strong> the Ports through construction <strong>of</strong> additional jetties, riprap-supported piers, <strong>and</strong> the Cabrillo<br />

Shallow Water Habitat. Assuming that portions <strong>of</strong> the historically described kelp beds located<br />

a<strong>long</strong> the outer breakwater are perennial <strong>and</strong> reproductive, they have likely contributed to the<br />

development <strong>of</strong> kelp communities elsewhere in the Ports. Persistent kelp beds adjacent to the<br />

outer breakwater, a<strong>long</strong> with the expansion <strong>of</strong> kelp forests <strong>of</strong>f the Pa<strong>los</strong> Verdes Peninsula, likely<br />

represent a consistent supply <strong>of</strong> sporophytes <strong>and</strong> gametophytes that can establish new kelp<br />

communities in the Ports.<br />

Scientific investigations <strong>of</strong> kelp forest habitats within the Ports have been limited to a kelp forest<br />

productivity study (fauna only) performed by MEC in 1986-87 (MEC 1988) <strong>and</strong> the previous<br />

2000 baseline study (MEC 2002). The 2000 baseline study was the first systematic effort to<br />

quantify kelp surface canopy coverage throughout the Ports. The total mapped canopy cover <strong>of</strong><br />

Macrocystis in the spring <strong>of</strong> 2000 was 24.8 acres, which decreased to 14.2 acres in fall 2000.<br />

During the present baseline study, the Macrocystis canopy totaled 77.8 acres in spring <strong>2008</strong><br />

<strong>and</strong> decreased to 50.4 acres in the fall <strong>of</strong> <strong>2008</strong>. Kelp die-<strong>of</strong>f between winter <strong>and</strong> fall can explain<br />

seasonal declines in kelp canopy cover for both the 2000 <strong>and</strong> <strong>2008</strong> studies. The 2000 baseline<br />

study reported a 43% decrease in canopy cover between spring <strong>and</strong> fall <strong>surveys</strong> compared to<br />

35% decrease in <strong>2008</strong>. Total mapped canopy cover <strong>of</strong> Macrocystis in the spring <strong>of</strong> <strong>2008</strong> was<br />

over 300% greater than reported in the spring <strong>of</strong> 2000, with kelp canopy cover being identified in<br />

several new areas within the Ports.<br />

New kelp beds in the Port <strong>of</strong> Los Angeles that were not noted during the 2000 survey included a<br />

large, dense bed adjacent to the Fish Harbor entrance, kelp canopy cover associated with the<br />

Cabrillo Shallow Water Habitat, <strong>and</strong> a bed east <strong>of</strong> the Angels Gate harbor entrance approaching<br />

the Port <strong>of</strong> Long Beach. Within the Port <strong>of</strong> Long Beach, kelp canopy cover near the entrance to<br />

the West Basin <strong>and</strong> a<strong>long</strong> Pier J increased dramatically in the present study compared to the<br />

<strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors 7–7<br />

April 2010

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