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Operational Plan for the Restoration of Diadromous Fishes to the ...

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Salmon catch/day<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

Salmon catch/day Percent scarred<br />

1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000<br />

Year<br />

Figure 1. Incidence <strong>of</strong> scars and trapnet catch rates <strong>of</strong> salmon on spawning<br />

runs at Long Pond, Kennebec County, 1988-2000.<br />

Nor<strong>the</strong>rn Pike in S<strong>to</strong>ny Brook: MDIFW Region B biologists surveyed Long Pond<br />

tributaries in Mount Vernon <strong>for</strong> <strong>the</strong> first time on August 15, 2005. Long Pond is<br />

actively s<strong>to</strong>cked with fall yearling landlocked salmon and spring yearling brook trout.<br />

S<strong>to</strong>ny Brook and two proximate unnamed tributaries were surveyed <strong>to</strong> document fish<br />

species composition and general fish habitat condition in 2005. Small sized (127-<br />

229 mm length range) nor<strong>the</strong>rn pike were documented in <strong>the</strong> two streams closest <strong>to</strong><br />

Long Pond, S<strong>to</strong>ny Brook and an unnamed tributary <strong>to</strong> Long Pond. Water<br />

temperatures at all sites were adequate <strong>for</strong> coldwater species management and are<br />

likely used as <strong>the</strong>rmal refuges by young pike and brook trout (Figure 2).<br />

S<strong>to</strong>ny Brook continues <strong>to</strong> be moni<strong>to</strong>red and is frequently surveyed by backpack<br />

electr<strong>of</strong>ishing <strong>to</strong> assess fish community composition at various times <strong>of</strong> <strong>the</strong> year<br />

(Table 2). The sample site is located downstream from <strong>the</strong> crossing with Belgrade<br />

Road and <strong>the</strong> existing road-stream crossing culvert is impassable <strong>to</strong> upstream fish<br />

movement. Nor<strong>the</strong>rn pike have been collected at all survey events in June, July,<br />

August and early September. Pike in S<strong>to</strong>ny Brook typically range from 65 – 195 mm<br />

and represent young <strong>of</strong> <strong>the</strong> year (YOY), or perhaps 1+ age fish. Three wild brook<br />

trout (size range 142 – 164 mm) were collected during <strong>the</strong> April 2007 sampling event<br />

only and are presumed <strong>to</strong> have dropped down from S<strong>to</strong>ny Brook’s upper reaches.<br />

Across all sampling events, water temperatures range from 11.0C (Sept 07) – 21.8C<br />

(Aug 05) and appear <strong>to</strong> maintain adequate <strong>the</strong>rmal regimes throughout summer <strong>for</strong><br />

coldwater species management.<br />

The pattern <strong>of</strong> small sized pike present in S<strong>to</strong>ny Brook during <strong>the</strong> summer months is<br />

consistent with juvenile pike using <strong>the</strong> stream as a refuge. S<strong>to</strong>ny Brook is a small<br />

stream with an average width <strong>of</strong> 4.5m and does not provide adequate habitat or<br />

water depth <strong>for</strong> larger sized pike. It is likely that S<strong>to</strong>ny Brook acts as both a <strong>the</strong>rmal<br />

refuge and as a spatial refuge <strong>for</strong> small sized nor<strong>the</strong>rn pike from Long Pond. Pike<br />

PRFP Page 216<br />

80<br />

70<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

% salmon with scars

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