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Petition to List Lynn Canal Pacific Herring under the Endangered ...

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<strong>the</strong> commercial fishery in <strong>Lynn</strong> <strong>Canal</strong> has been closed; for 2001-2003, <strong>the</strong> spawning<br />

biomass estimate was less than 1,000 <strong>to</strong>ns and a more precise estimate for 2004 was 743<br />

<strong>to</strong>ns based on survey dives <strong>to</strong> measure egg density (M. Pritchett, pers comm). Along with<br />

declines in biomass estimates, <strong>the</strong> geographic extent of <strong>the</strong> population’s spawning<br />

grounds has also declined. From 1972 <strong>to</strong> 1989, herring spawn was observed in Auke Bay<br />

in 14 out of <strong>the</strong> 18 years, or 78% of <strong>the</strong> time. However, 1989 was <strong>the</strong> last year that<br />

herring spawn was observed in Auke Bay, and no spawning activity has been observed<br />

south of Yankee Cove for <strong>the</strong> past 15 years (M. Pritchett, pers comm.). Based on <strong>the</strong><br />

information available, it seems likely that abandonment of <strong>the</strong> Auke Bay spawning<br />

grounds was caused by a combination of fac<strong>to</strong>rs, including increased shoreline<br />

development in <strong>the</strong> bay, declines in water quality, and low numbers of herring available<br />

<strong>to</strong> spawn and rebuild <strong>the</strong> s<strong>to</strong>ck (Wing, pers comm.,Koski, pers comm.). Continuing trends<br />

in small population size and <strong>the</strong> lack of steady population growth despite <strong>the</strong> fishery’s<br />

closure suggest that a population bottleneck may have occurred.<br />

(NMFS 2005: 59). Similarly, <strong>the</strong> Alaska Dept. of Fish and Game has summarized <strong>the</strong> status of<br />

<strong>the</strong> population in equally dire terms (ADFG 2004):<br />

Prior <strong>to</strong> 1983, <strong>the</strong> <strong>Lynn</strong> <strong>Canal</strong> herring s<strong>to</strong>ck was one of <strong>the</strong> larger s<strong>to</strong>cks in Sou<strong>the</strong>ast<br />

Alaska supporting several commercial fisheries including a sac roe fishery, bait pound<br />

fishery, and a winter food and bait fishery. <strong>Lynn</strong> <strong>Canal</strong> herring traditionally spawned<br />

from Auke Bay <strong>to</strong> Point Sherman. This s<strong>to</strong>ck declined in 1982 and has since remained at<br />

low and variable levels as evidenced from estimates of linear measurements of shoreline<br />

that receive spawn. The reason for <strong>the</strong> decline is not clear, however, potential candidates<br />

are overfishing, habitat degradation and/or disturbance in Auke Bay, geographic shifting<br />

of spawning aggregations, population growth of major preda<strong>to</strong>rs such as sea lions, or a<br />

combination of <strong>the</strong>se. If <strong>the</strong> decline is attributable solely <strong>to</strong> overfishing, it is puzzling<br />

that <strong>the</strong>re has been no apparent recovery or re-establishment of this s<strong>to</strong>ck during a 20-<br />

year absence of exploitation. In o<strong>the</strong>r areas in Sou<strong>the</strong>ast Alaska, such as West Behm<br />

<strong>Canal</strong>, herring s<strong>to</strong>cks have grown from low levels <strong>to</strong> very high levels over a span of a few<br />

years.<br />

The documented spawn for <strong>the</strong> <strong>Lynn</strong> <strong>Canal</strong> herring s<strong>to</strong>ck from 1953 <strong>to</strong> 1981 ranged from<br />

6 <strong>to</strong> 28 nautical miles averaging approximately 12 miles. Significant spawning occurred<br />

in <strong>the</strong> vicinity of Auke Bay. In recent years however <strong>the</strong> entire <strong>Lynn</strong> <strong>Canal</strong> herring s<strong>to</strong>ck<br />

has centered its spawn activity between Pt. Bridget and <strong>the</strong> Berners Bay flats. Since 1982<br />

<strong>the</strong> documented spawn has ranged from 0.5 <strong>to</strong> 7 nautical miles averaging only 3.5<br />

nautical miles. The established biomass threshold level for this s<strong>to</strong>ck is 5,000 <strong>to</strong>ns of<br />

spawning biomass. This means that before a herring fishery may be considered for <strong>the</strong><br />

<strong>Lynn</strong> <strong>Canal</strong> s<strong>to</strong>ck, a forecast spawning biomass must meet or exceed 5,000 <strong>to</strong>ns. Based<br />

on shoreline miles of spawn, it is estimated that <strong>the</strong> s<strong>to</strong>ck biomass has varied between<br />

100 and 2,500 <strong>to</strong>ns over <strong>the</strong> last 20 years. Studies of herring over-wintering in <strong>the</strong> Juneau<br />

area have continued over <strong>the</strong> years in an attempt <strong>to</strong> reconcile acoustical observations of<br />

biomass with estimates of spawning biomass, and <strong>to</strong> moni<strong>to</strong>r age composition of <strong>the</strong><br />

s<strong>to</strong>ck.<br />

14

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