Marine Resources Assessment for the Marianas Operating ... - SPREP
Marine Resources Assessment for the Marianas Operating ... - SPREP
Marine Resources Assessment for the Marianas Operating ... - SPREP
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AUGUST 2005 FINAL REPORT<br />
and weigh 170 to 240 kilograms [kg], with females growing slightly larger than males (Gilmartin and<br />
Forcada 2002). O<strong>the</strong>r than this size difference, <strong>the</strong>re is little noticeable sexual dimorphism. Coloration<br />
of Hawaiian monk seals is drab, generally a yellow-brown to silvery gray color with slight<br />
countershading and some small ventral white patches.<br />
Status—The Hawaiian monk seal is listed as endangered under <strong>the</strong> ESA and depleted under <strong>the</strong><br />
MMPA (Ragen and Lavigne 1999). The Hawaiian monk seal population is a NOAA Fisheries strategic<br />
stock (Carretta et al. 2004). Hawaiian monk seals are managed as a single stock, although <strong>the</strong>re are<br />
six main reproductive subpopulations at French Frigate Shoals, Laysan Island, Lisianski Island, Pearl<br />
and Hermes Reef, Midway Island, and Kure Atoll (Ragen and Lavigne 1999; Carretta et al. 2004).<br />
Genetic comparisons between <strong>the</strong> Northwestern and main Hawaiian Islands seals have not yet been<br />
conducted, but observed interchange of individuals among <strong>the</strong> regions is extremely rare, suggesting<br />
that <strong>the</strong>se may be more appropriately designated as separate stocks; fur<strong>the</strong>r research is needed<br />
(Carretta et al. 2004).<br />
The best estimate of <strong>the</strong> total population size is 1,304 individuals (Carretta et al. 2004). In 2001, <strong>the</strong>re<br />
were an estimated 52 seals in <strong>the</strong> main Hawaiian Islands (Baker and Johanos 2004; Carretta et al.<br />
2004); <strong>the</strong> vast majority of <strong>the</strong> population occurs in <strong>the</strong> Northwestern Hawaiian Islands. The trend in<br />
abundance <strong>for</strong> <strong>the</strong> population over <strong>the</strong> past 20 years has mostly been negative (Baker and Johanos<br />
2004; Carretta et al. 2004). A self-sustaining subpopulation in <strong>the</strong> main Hawaiian Islands may<br />
improve <strong>the</strong> monk seal’s long-term prospects <strong>for</strong> recovery (MMC 2003; Baker and Johanos 2004;<br />
Carretta et al. 2004).<br />
Critical habitat <strong>for</strong> <strong>the</strong> Hawaiian monk seal is designated from <strong>the</strong> shore out to 37 m (20 fathoms) in<br />
10 areas of <strong>the</strong> Northwestern Hawaiian Islands (NMFS 1988) (Figure 3-2).<br />
Habitat Preferences—Breeding habitat <strong>for</strong> <strong>the</strong> Hawaiian monk seal primarily consists of short, sandy<br />
beaches, although hard substrate beach areas and exposed reef are used at some islands (Gilmartin<br />
1983). Dry sand areas above <strong>the</strong> high tide line are preferred (Kenyon 1973; Gilmartin 1983). The<br />
breeding beaches are characterized by shallow, protected water adjacent to <strong>the</strong> shoreline, which may<br />
limit access by large predatory sharks (Westlake and Gilmartin 1990). Foraging habitat is commonly<br />
restricted to waters of less than 100 m in depth near <strong>the</strong> breeding atolls and seamounts (Parrish et al.<br />
2000; Stewart 2004). The inner reef waters adjacent to <strong>the</strong> islands are critical to weaned pups<br />
learning to feed, as <strong>the</strong> pups move laterally along <strong>the</strong> shoreline, but do not appear to travel far from<br />
shore during <strong>the</strong> first few months after weaning (Gilmartin 1983). Feeding has been observed in reef<br />
caves (Gilmartin 1983). Recent studies have shown that adult seals at French Frigate Shoals <strong>for</strong>age<br />
at depths of 300 to 500 m in deepwater coral beds (Parrish et al. 2002), and 2 to 3 year-olds feed at<br />
much shallower depths of 10 to 30 m (Parrish et al. 2005). However, juveniles feed in water sand<br />
fields with a bottom depth of 50 to 100 m on <strong>the</strong> atoll’s outer slope (Parrish et al. 2005).<br />
Local environmental conditions affect trends in abundance of specific monk seal subpopulations, with<br />
areas sharing similar ecological characteristics having similar trends (Schmelzer 2000). Climatedriven<br />
changes in oceanic productivity could be decisive in reducing (or enhancing) monk seal<br />
reproduction and survival. Juvenile seals feed over deepwater sand fields, and oceanographic<br />
conditions are thought to influence survivorship of <strong>the</strong>se seals (Parrish et al. 2005). Polovina et al.<br />
(1994) speculated that climate changes in <strong>the</strong> central North Pacific cause declines in lobster<br />
recruitment, which contributed to declines in <strong>the</strong> numbers of monk seal pups. More recent work<br />
suggests that El Niño conditions may actually benefit Hawaiian monk seals by making prey more<br />
available and resulting in weaned pups with larger axillary girths (and <strong>the</strong>re<strong>for</strong>e, presumably, better<br />
nutritional condition) (Antonelis et al. 2003). Fur<strong>the</strong>r research is needed to fully understand <strong>the</strong><br />
implications of climate change on this species.<br />
Distribution—The Hawaiian monk seal occurs only in <strong>the</strong> central North Pacific. Until recently, this<br />
species occurred almost exclusively at remote atolls in <strong>the</strong> Northwestern Hawaiian Islands where six<br />
major breeding colonies are located: French Frigate Shoals, Laysan and Lisianski Islands, Pearl and<br />
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