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Marine Fish and Benthos Studies - Knik Arm Bridge and Toll Authority

Marine Fish and Benthos Studies - Knik Arm Bridge and Toll Authority

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species of polychaete worm, Neanthes limnicola, for a total of just nine taxa.<br />

Another isopod, Argeia pugettensis, is parasitic on crangonid shrimp <strong>and</strong> thus is<br />

not a true member of the invertebrate assemblage. In addition, parasitic sea lice<br />

of the copepod Family Caligidae, were often seen in the net following capture of<br />

adult salmon.<br />

Consistent among the 1983, 2004, <strong>and</strong> 2005 sampling efforts is a trend of<br />

increasing abundance in overall invertebrate densities beginning from spring <strong>and</strong><br />

moving into fall. In 2004 through 2005 this trend was significant (P = 0.000;<br />

Figure 25, Appendix B, Tables B-1 <strong>and</strong> B-4). Overall, CPUE was greatest during<br />

late summer/fall (August through October) 2004 in comparison to either the<br />

1983 or spring/summer 2005 surveys. When overall CPUE data for April<br />

through July 2005 are combined with data from July through November 2004,<br />

CPUE increases steadily over the combined year, with the exception of<br />

November 2004. A sharp decline in total invertebrate catch in November was<br />

in part, the result of the large quantity of gray ice shards captured by the net in<br />

most sets. The color <strong>and</strong> size of these shards mimicked the small clear or pale<br />

gray bodied invertebrates <strong>and</strong> made their collection very ineffective. However,<br />

CPUE in November 2004 was similar to that in early spring (April 2005) when<br />

ice was not a factor. Thus, there appears to have been a real drop in<br />

invertebrate presence during the winter (November through April).<br />

Early in the 2005 survey, the amphipod Lagunogammarus setosus dominated the<br />

catch, but its dominance was replaced by Crangon franciscorum in early May.<br />

The overall CPUE of Crangon species continued to increase throughout the<br />

study period, but the dominant species C. franciscorum, dropped off significantly<br />

in July (P = 0.000, Appendix Table B-4) <strong>and</strong> was replaced by a newly emerged<br />

cohort of Crangon. It is probable that this new cohort also was C. franciscorum,<br />

based on the progression of CPUE shown on Figure 26, but identification could<br />

not be confirmed due to small size <strong>and</strong> lack of maturity. Mysid abundance was<br />

relatively constant over the sampling period (Figure 26) until July when CPUE of<br />

mysids reached their peak in both years sampled (P = 0.000 in 2005; Appendix<br />

Table B-4). Species dominance shifted from Neomysis mercedis to N. rayii at the<br />

end of June <strong>and</strong> continued through July (Figure 26).<br />

Over the entire 2005 survey period, the mean invertebrate CPUE at each station<br />

sampled (averaged over time) ranged from 21.5 per set (KA 5) to over 120 per<br />

set (KA 2), but combined species CPUE did not vary significantly (Appendix<br />

Tables B-2, B-3, <strong>and</strong> B-4). The sites with the greatest CPUE were dominated by<br />

crangonid shrimp <strong>and</strong> were located at the northern reach of <strong>Knik</strong> <strong>Arm</strong> (sites<br />

KA 2, KA 6, <strong>and</strong> KA 10; Figure 27, Appendix B). The only group of invertebrates<br />

that varied significantly by station was the amphipods, which were most<br />

prevalent at KA 13.<br />

Pentec Environmental Page 31<br />

12214-12 November 30, 2005

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