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

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8.0 Eelgrass<br />

8.0 EELGRASS<br />

8.1 INTRODUCTION<br />

The primary objective <strong>of</strong> this task<br />

was to characterize the occurrence<br />

<strong>of</strong> eelgrass beds within the Ports <strong>of</strong><br />

Los Angeles <strong>and</strong> Long Beach (Ports)<br />

<strong>and</strong> compare changes in eelgrass<br />

bed extent <strong>and</strong> density since the last<br />

baseline survey (MEC 2002).<br />

Seagrasses (Spermatophyta) inhabit<br />

s<strong>of</strong>t bottom habitat, <strong>and</strong> the<br />

extensive meadows they form rank<br />

among the most productive coastal<br />

ecosystems in the world (McRoy <strong>and</strong><br />

McMillan 1977). Of the three<br />

separate species <strong>of</strong> seagrass<br />

(Zostera marina, Z. pacifica, <strong>and</strong> Z.<br />

asiatica) that have been observed in<br />

the Southern California Bight (SCB),<br />

eelgrass (Zostera marina) is the most common species occurring in embayments (Dailey et al.<br />

1993).<br />

Eelgrass is an aquatic angiosperm distributed sporadically in bays, estuaries, <strong>and</strong> within<br />

<strong>of</strong>fshore beds throughout the majority <strong>of</strong> the Northern Hemisphere. A<strong>long</strong> the west coast <strong>of</strong><br />

North America, eelgrass is found from southeastern Alaska to southern Baja California <strong>and</strong><br />

Mexico, typically in protected bays <strong>and</strong> estuaries from the low intertidal to a depth <strong>of</strong><br />

approximately 20 meters (m) (Green <strong>and</strong> Short 2003). Eelgrass beds create a defined<br />

community structure for a wide variety <strong>of</strong> aquatic organisms <strong>and</strong> perform important physical <strong>and</strong><br />

<strong>biological</strong> functions that allow for the persistence <strong>of</strong> highly productive habitat. Eelgrass beds<br />

function as habitat <strong>and</strong> nursery areas for commercially <strong>and</strong> recreationally important marine fish<br />

<strong>and</strong> invertebrates, <strong>and</strong> provide critical structural environments for resident bay <strong>and</strong> estuarine<br />

species (H<strong>of</strong>fman 1986, Kitting 1994). Their function as nursery areas for fish <strong>and</strong> invertebrates<br />

<strong>and</strong> as foraging grounds for many marine bird species make eelgrass beds highly valuable as a<br />

marine resource far beyond their physical extent.<br />

Eelgrass is important both ecologically <strong>and</strong> economically, representing a key species in<br />

maintaining healthy coastal <strong>and</strong> estuary ecosystems (Davis et al. 1998, Gayaldo et al. 2001,<br />

<strong>and</strong> Williams 2001).<br />

Eelgrass reproduces sexually through seeds <strong>and</strong> asexually through horizontal rhizomes <strong>and</strong> leaf<br />

shoots. Although dispersal <strong>of</strong> pollen <strong>and</strong> individual seeds is limited, genetic studies have shown<br />

that the seed-bearing spathes can be transported from one area to another via rafting <strong>of</strong><br />

detached plants or inflorescences (Reusch 2002). Although considerable attention has been<br />

given to limitations <strong>of</strong> seagrass growth by variability in light, temperature, <strong>and</strong> nutrients (e.g.,<br />

McRoy <strong>and</strong> McMillan 1977, Orth 1977, Williams <strong>and</strong> McRoy 1982, Dennison <strong>and</strong> Alberte 1985,<br />

<strong>and</strong> Dennison 1987), growth is affected by a more complex array <strong>of</strong> factors including hydrology,<br />

grazing, <strong>and</strong> epiphytic growth (Fonseca <strong>and</strong> Kenworthy 1987, Thayer et al. 1985, Williams <strong>and</strong><br />

Carpenter 1988, Williams <strong>and</strong> Ruckelshaus 1993). As water quality in many bay <strong>and</strong> coastal<br />

environments declines due to increases in anthropogenic nutrient <strong>and</strong> sediment loading, the<br />

<strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors 8–1<br />

April 2010

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