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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 />

sediment used to develop the shallow water habitat supported kelp in the spring (Figure 7.3-1)<br />

but not during the fall <strong>surveys</strong> (Figure 7.3-3). Additionally, the kelp surface canopy associated<br />

with the largest kelp bed near the entrance to Fish Harbor was noticeably reduced between the<br />

spring <strong>and</strong> fall <strong>surveys</strong> (Figure 7.3-1 <strong>and</strong> 7.3-3). Similar differences in kelp canopy spatial<br />

extent was observed in the Port <strong>of</strong> Long Beach between spring <strong>and</strong> fall, including reduced kelp<br />

canopy cover <strong>and</strong> density near the boundary line between the Ports <strong>of</strong> Los Angeles <strong>and</strong> Long<br />

Beach <strong>and</strong> a reduced width <strong>of</strong> delineated kelp canopy areas just shoreward <strong>of</strong> the Port <strong>of</strong> Long<br />

Beach entrance (Figures 7.3-2 <strong>and</strong> 7.3-4).<br />

The categorization <strong>of</strong> surface canopy densities within polygons provides a summary <strong>of</strong> the total<br />

st<strong>and</strong>ing stock <strong>of</strong> kelp canopy observed during <strong>surveys</strong> <strong>and</strong> ultimately available for utilization by<br />

associated invertebrates, fish, <strong>and</strong> wildlife.<br />

Temporal fluctuations <strong>of</strong> kelp canopy cover <strong>and</strong> density within the Ports follow typical southern<br />

California seasonal trends observed between late winter <strong>and</strong> early fall (Dayton et al. 1999, North<br />

1994, among others). Factors affecting the degree <strong>of</strong> change <strong>of</strong> kelp canopy st<strong>and</strong>ing stock<br />

within the Ports are complex but likely involve oceanic circulation <strong>and</strong> large-scale movements <strong>of</strong><br />

regional water masses within the Southern California Bight.<br />

During the spring <strong>surveys</strong>, kelp plants appeared healthy, dense, <strong>and</strong> more c<strong>los</strong>ely spaced. Kelp<br />

fronds (blades) contained low epiphyte loads <strong>and</strong> displayed few signs <strong>of</strong> stress or senescence.<br />

Surveys <strong>of</strong> the same locations in fall found fewer, smaller kelp plants that were more widely<br />

spaced <strong>and</strong> heavily infested with epiphytic bryozoans. Overall, kelp plants observed in the fall<br />

had fewer stipes <strong>and</strong> fronds, thus showing signs <strong>of</strong> stress <strong>and</strong> deterioration. In kelp beds,<br />

stratification in the water column during summer results in a warm, nutrient-poor environment<br />

above the thermocline <strong>and</strong> cool, nutrient-enhanced conditions below (North 1983).<br />

Consequently, kelp deterioration is greatest in the surface layers while basal portions may<br />

survive with little, if any, damage. When sea surface temperatures fall during autumn, basal<br />

portions may regenerate the canopies in a few weeks or months (North 1983). In addition, the<br />

fall <strong>surveys</strong> may have been too early to document any basal regeneration. Nutrient availability<br />

is negatively correlated with water temperature for values greater than 15.5°C (Zimmerman,<br />

1983). Consequently, reported observations <strong>of</strong> summertime deterioration by Macrocystis<br />

attributed to high temperature probably represent combined effects from elevated water<br />

temperatures <strong>and</strong> low nutrients (Jackson 1977, Zimmerman <strong>and</strong> Kremer 1984).<br />

The observed seasonal changes are to be expected in view <strong>of</strong> the elevated water temperatures,<br />

reduced water circulation, <strong>and</strong> low nutrient concentrations typical <strong>of</strong> the summer months in<br />

southern California, especially in enc<strong>los</strong>ed bays <strong>and</strong> estuaries. Overall, seasonal decreases in<br />

the extent <strong>and</strong> density <strong>of</strong> the kelp surface canopy also reduce primary <strong>and</strong> secondary<br />

productivity, <strong>and</strong> habitat for associated biota. However, even though seasonal decreases are<br />

evident, the persistence <strong>of</strong> some kelp canopy in the majority <strong>of</strong> surveyed areas stabilizes<br />

community structure <strong>and</strong> species composition, increases the probability that more plants will<br />

settle, <strong>and</strong> enhances recruitment <strong>of</strong> dependent invertebrates <strong>and</strong> fishes.<br />

The Ports are near healthy kelp forests to the north, near Pa<strong>los</strong> Verdes, that likely provide a<br />

steady supply <strong>of</strong> sporophytes <strong>and</strong> gametophytes for colonization <strong>of</strong> suitable areas <strong>of</strong> the Ports.<br />

For example, the 2000 baseline study noted relatively rapid colonization <strong>of</strong> kelp plants during<br />

the construction <strong>of</strong> Pier 400 (MEC 2002). Similar recruitment events have been noted near<br />

Cabrillo Marina, where substrate is commonly covered <strong>and</strong> uncovered by winter storms, thereby<br />

making new suitable substratum available for settlement.<br />

<strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors 7–5<br />

April 2010

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