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3.0 Affected Environment - Knik Arm Bridge and Toll Authority

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<strong>Knik</strong> <strong>Arm</strong> Crossing DraftFinal EIS<br />

<strong>Affected</strong> <strong>Environment</strong><br />

Table 3-29. Essential fish habitat designations <strong>and</strong> presence in the <strong>Knik</strong> <strong>Arm</strong><br />

portion of the Study Area<br />

Groundfish <strong>and</strong><br />

forage fish<br />

species<br />

Egg<br />

Larvae<br />

Late<br />

juvenile a, b Adulta, b Spawning<br />

Pacific cod • c • c<br />

Sculpin spp. • c •<br />

Walleye pollock • • c<br />

Eulachon • •<br />

Pacific Salmon<br />

species<br />

Egg <strong>and</strong><br />

larvae<br />

(fresh<br />

water d )<br />

Juvenile<br />

(fresh<br />

water d )<br />

Juvenile<br />

estuarine b )<br />

Adult<br />

(marine<br />

waters b )<br />

Spawning<br />

(freshwater<br />

only d )<br />

Chinook salmon • •<br />

Chum salmon • •<br />

Coho salmon • • •<br />

Pink salmon • • •<br />

Sockeye salmon • • •<br />

a<br />

NOAA Fisheries, 2005<br />

b<br />

KABATA, 2005<br />

c<br />

Designated as EFH, but not captured in any studies in <strong>Knik</strong> <strong>Arm</strong><br />

d<br />

ADF&G, 2005<br />

Juveniles <strong>and</strong> adults of all five Pacific salmon species are present in <strong>Knik</strong> <strong>Arm</strong> as well as in<br />

more than a dozen streams <strong>and</strong> rivers that discharge into Upper Cook Inlet. Analysis of<br />

length, frequency, <strong>and</strong> timing patterns suggests that juvenile pink <strong>and</strong> chum salmon move<br />

through <strong>Knik</strong> <strong>Arm</strong> relatively quickly <strong>and</strong> do not grow much in this environment. On the other<br />

h<strong>and</strong> <strong>Knik</strong> <strong>Arm</strong> may be important rearing habitat for the juvenile coho, chinook, <strong>and</strong> sockeye<br />

salmon emerging from streams <strong>and</strong> rivers that discharge into <strong>Knik</strong> <strong>Arm</strong>. Juveniles of these<br />

species appear to be feeding <strong>and</strong> growing actively in <strong>Knik</strong> <strong>Arm</strong> into August (FHWA <strong>and</strong><br />

ADOT&PF 1983a; Moulton 1997; KABATA 2005b; Pentec 2005).<br />

Juvenile salmon use of both shoreline <strong>and</strong> mid-channel habitats in <strong>Knik</strong> <strong>Arm</strong> differs from<br />

that of juvenile salmon use of clearwater estuaries (KABATA 2005b), where early<br />

out-migrants are found primarily residing in nearshore habitats (see reviews by Salo 1991;<br />

S<strong>and</strong>ercock 1991; Healey 1991). A comparison of beach seining <strong>and</strong> tow net data as catch<br />

per unit effort (CPUE), which accounts for bias in relative effort for differences in sampling<br />

efficiency associated with various sampling gear types, suggests a shoreline or intertidal<br />

preference by juvenile chinook <strong>and</strong> coho salmon. Juveniles of chum <strong>and</strong> sockeye salmon<br />

appear to use both nearshore <strong>and</strong> mid-channel habitats, with a markedly higher occurrence in<br />

mid-channel habitat. Juvenile pink salmon were primarily found in mid-channel habitat<br />

(KABATA 2005b).<br />

3-198 12/18/07

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