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

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3.0 Adult <strong>and</strong> Juvenile Fishes<br />

species were subsampled using the same methods described above for lampara sampling.<br />

Macroinvertebrates collected from trawl <strong>surveys</strong> were identified to the lowest practicable taxon,<br />

counted, <strong>and</strong> an aggregate weight determined by species.<br />

Identification <strong>of</strong> invertebrates was aided by a combination <strong>of</strong> photography <strong>and</strong> collection <strong>of</strong><br />

voucher specimens for taxa that could not be identified in the field. Voucher specimens were<br />

preserved as noted for the benthic collections <strong>and</strong> <strong>final</strong> identifications, based on photographs<br />

<strong>and</strong>/or voucher specimens, were made by taxonomic specialists.<br />

3.2.3 Shallow Subtidal (Beach Seine) Fishes<br />

Fish sampling in shallow-water s<strong>and</strong>y habitats was conducted<br />

using a 15.2 m <strong>long</strong> by 1.8 m deep beach seine net. The net<br />

had 0.6 cm mesh wings with a bag end <strong>of</strong> 0.3 cm mesh. The<br />

fish catch was processed in the field. Every specimen was<br />

identified <strong>and</strong> counted, except when abundant species were<br />

encountered. If more than 30 individuals from one species<br />

was collected, the same protocols used for trawl <strong>and</strong> lampara<br />

sampling were followed (see Section 3.2.1). After field<br />

processing was completed, all specimens were immediately<br />

returned to the water to reduce potential mortality.<br />

3.2.4 Data Analysis<br />

All fish data were entered into a database which included unique species codes, count, length,<br />

<strong>and</strong> weight data. In addition, the fish database was subjected to st<strong>and</strong>ardized quality assurance<br />

routines. Consistent with the previous baseline survey analyses, abundance <strong>and</strong> biomass<br />

values in this report are presented as catch per unit effort (CPUE), that is, catch in one set <strong>of</strong><br />

the lampara net, otter trawl, or beach seine. Fish length data were st<strong>and</strong>ardized to onecentimeter<br />

size classes.<br />

Community measures <strong>of</strong> species richness <strong>and</strong> diversity were calculated using CPUE values <strong>and</strong><br />

included number <strong>of</strong> species, Shannon-Wiener diversity, Margalef diversity, <strong>and</strong> Dominance.<br />

Diversity indices <strong>and</strong> Dominance were calculated using the following formulas:<br />

• Number <strong>of</strong> species or unique taxa;<br />

• Shannon-Wiener diversity: -Σp i X ln(p i ), where p i is the count for species i;<br />

• Margalef diversity: (S-1)/ln(n), where S is the number <strong>of</strong> taxa, <strong>and</strong> n is the number <strong>of</strong><br />

individuals; <strong>and</strong><br />

• Dominance: number <strong>of</strong> species comprising 75% <strong>of</strong> the total count <strong>of</strong> the sample.<br />

Analysis <strong>of</strong> variance (ANOVA) was performed on log-transformed (natural log = ln) abundance<br />

<strong>and</strong> biomass data to determine whether there were significant differences in catch between day<br />

<strong>and</strong> night <strong>and</strong>/or among seasons. ANOVA was also used to test for seasonal <strong>and</strong> diurnal<br />

differences in catches.<br />

<strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors 3–3<br />

April 2010

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