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Vol. 53 - Alaska Resources Library and Information Services

Vol. 53 - Alaska Resources Library and Information Services

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ecology of young juveniles in Dutch Harbor that, along with descriptions<br />

of habitat occupied around Kodiak Isl<strong>and</strong> (Jewett <strong>and</strong> Powell 1981; Powell<br />

<strong>and</strong> Nickerson 1965) <strong>and</strong> in Kachemak Bay (Sundberg <strong>and</strong> Clausen 1979) has<br />

led to a hypothesis of strict habitat requirements for survival (Armstrong<br />

1983; Armstrong, et al. 1983b). A working hypothesis in the<br />

beginning of the present study was that O+ juveniles require substrate<br />

that affords both refuge from predators <strong>and</strong> adequate food (e.g. shell,<br />

cobble, biological materials such as tube worms). The link between the<br />

location of megalops larvae at metamorphosis <strong>and</strong> appropriate bottom<br />

material was viewed as one critical determinant of year class strength.<br />

Location of such refuge substrate <strong>and</strong> 0+ to 1+ juveniles was found<br />

previously to be very difficult along the NAS. During a 1982 OCSEAP<br />

project to study feeding habits of small juvenile red king crab, almost<br />

no animals in this size range (about 5 to 25 mm carapace length) were<br />

found using nets, divers <strong>and</strong> underwater cameras (W. Pearson, Battelle NW<br />

Laboratories, pers. communication). The National Marine Fisheries<br />

Service has caught virtually no crab of this size in over a decade of<br />

extensive sampling (e.g. Otto, et al. 1982). Armstrong, et al. (1983b)<br />

attributed this to inappropriately large gear <strong>and</strong> little effort nearshore<br />

where they assumed this stage must be most common.<br />

Growth rates of 0+ <strong>and</strong> older juveniles have been studied <strong>and</strong> animals<br />

reach mean carapace lengths of about 11 mm, 35 mm, 60 mm <strong>and</strong> 80 mm at<br />

one, two, three <strong>and</strong> four years, respectively (Powell <strong>and</strong> Nickerson 1965;<br />

Weber 1967). Growth models for the species have been developed by<br />

McCaughran <strong>and</strong> Powell (1977), Reeves <strong>and</strong> Marasco (1980) <strong>and</strong> Weber<br />

(1967). Young-of-the-year molt from eight (Powell 1967) to 11 (Weber<br />

1967) times in the first year. Such a high frequency of molting could<br />

make them particularly susceptible to nearshore oil pollution since<br />

ecdysis is the time of greatest sensitivity to toxicant stress (Armstrong,<br />

et al. 1976; Karinen 1981).<br />

292

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