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

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4.0 Ichthyoplankton<br />

The ichthyoplankton stations were designated as being in one <strong>of</strong> three general areas (Table<br />

4.4-2): deep outer harbor (seven stations), shallow outer harbor (four stations), <strong>and</strong> inner harbor<br />

(eight stations). The average weighted mean abundance <strong>of</strong> larval fish in each <strong>of</strong> these three<br />

areas was: shallow outer harbor 1,523/100m 2 , inner harbor 1,297/m 2 , <strong>and</strong> deep outer harbor<br />

1,157/100m 2 . The range <strong>of</strong> values in each area was variable; for example, the value for the<br />

shallow outer area was the highest based on the large number <strong>of</strong> larvae found at station LA7<br />

(4,381/100m 2 in Tables 4.3-3 <strong>and</strong> 4.3-5). The other three stations designated shallow outer<br />

were much lower ranging from 257 to 588 larvae/100m 2 .<br />

4.5 METHOD COMPARISON STUDY RESULTS<br />

The comparison <strong>of</strong> the two sampling approaches was based on two analyses. First, total larval<br />

abundance (#/100m 2 ) in paired samples (three-net sampling vs. CalCOFI-type sampling - Table<br />

4.5-1) was compared by calculating the difference between the two samples <strong>and</strong> testing the<br />

hypothesis that the average difference was zero. Since the differences were not normally<br />

distributed, abundance data were transformed (log 10 ) prior to calculating differences. As Table<br />

4.5-1 shows, the three-net method overall yielded somewhat higher abundances than the<br />

CalCOFI method, although in five <strong>of</strong> the twenty sample pairs abundances were lower in the<br />

three-net samples. The statistical analysis showed that the average difference was not<br />

significantly different from zero, but a power analysis showed that due to the small sample size<br />

<strong>and</strong> variation in the data, there was only a 7 percent chance that a difference from zero could<br />

have been detected. Since acceptable levels <strong>of</strong> power for such tests are 70 percent or greater,<br />

the results <strong>of</strong> this analysis do not support a comparison <strong>of</strong> the two methods.<br />

The second analysis compared the Bray-Curtis similarity between the paired samples collected<br />

using the two methods. The average similarity between the paired samples at the ten stations<br />

was 56.8 percent (Table 4.5-1). The average Bray-Curtis similarity among the 171 possible<br />

sample pairs based on the average abundances for the three <strong>surveys</strong> at all 19 stations was<br />

slightly higher, at 57.3 percent. The average similarity between paired samples at the ten<br />

stations would be expected to be much greater than the average based on a r<strong>and</strong>om sample <strong>of</strong><br />

all <strong>of</strong> the samples if the CalCOFI-type sampling was effective at replicating the sampling done<br />

with the three nets. Although the result <strong>of</strong> the statistical comparison was unable to detect a<br />

statistically significant difference between the two methods, the overall results were<br />

inconclusive.<br />

Due to the patchiness <strong>of</strong> plankton, filtering larger volumes <strong>of</strong> water increases the chance <strong>of</strong><br />

collecting a more representative cross section <strong>of</strong> the ichthyoplankton composition, but will also<br />

increase the sample processing time <strong>and</strong> cost. It is recommended that for future studies in the<br />

Port complex the current three-net method be continued with a modification to the midwater<br />

collection. It is suggested that the surface <strong>and</strong> epibenthic sampling continue without change.<br />

These techniques allow more water in these two strata to be filtered than does the CalCOFI<br />

technique. This increases the chance <strong>of</strong> collecting rare taxa that might be in higher<br />

concentrations in these two strata than in the midwater. However, it is recommended that the<br />

‘steps’ in the current midwater sampling be eliminated. These ‘steps’ introduce potential biases<br />

into the data by oversampling the depth strata where the net was during its ‘steps’. It is also<br />

impossible to replicate the exact depth strata used at each station or between <strong>surveys</strong> at a<br />

particular station due to factors such as vessel, wind, current speeds, <strong>and</strong> length <strong>of</strong> tow cable.<br />

Therefore, it is recommended that during any future midwater collection the net be deployed in a<br />

similar fashion to that used during the CalCOFI-type tows in this study, where the nets<br />

deployment <strong>and</strong> retrieval speeds through the water column be constant so that all depths are<br />

evenly sampled.<br />

<strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors 4–7<br />

April 2010

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