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

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(early life stages were weighted more than later life stages) or <strong>the</strong> reliability <strong>of</strong> <strong>the</strong><br />

parameter. A weighted rank (weighted sum <strong>of</strong> each parameter divided by <strong>the</strong> sum <strong>of</strong><br />

<strong>the</strong> weights) was developed <strong>for</strong> each waterbody and classified in<strong>to</strong> low, medium and<br />

high potential nor<strong>the</strong>rn pike habitat.<br />

The waterway model used a variation <strong>of</strong> that proposed by Inskip (1982) and used only<br />

stream and river hydraulic characteristics. Hydraulic-geometry relationships (Dudley<br />

2004 and Wright et al. 2008) were used <strong>to</strong> approximate waterway channel<br />

characteristics <strong>for</strong> <strong>the</strong> low flow period (average velocity, depth and gradient) <strong>for</strong> each<br />

stream or river in <strong>the</strong> watershed. The classification was completed <strong>for</strong> stream or river<br />

segments or reaches <strong>to</strong> allow <strong>for</strong> more continuous classification along <strong>the</strong> length <strong>of</strong> a<br />

particular waterway (see Wright et al. 2008). A habitat suitability index was calculated<br />

from four parameters in Table 5. Three <strong>of</strong> <strong>the</strong> parameters (parameters 10-12) were<br />

exclusionary (ei<strong>the</strong>r present or absent). Stream gradient (parameter 12) was assigned<br />

five values ranging from 0 (not suitable) <strong>to</strong> 1 (most suitable). A habitat suitable index<br />

(HSI) was developed <strong>for</strong> each waterway segment by multiplying each <strong>of</strong> <strong>the</strong> parameter<br />

values. The HSI was assigned a value from 0 (not suitable) <strong>to</strong> 1 (most suitable) <strong>for</strong> all<br />

<strong>the</strong> classified waterway segments.<br />

Results<br />

The results <strong>for</strong> <strong>the</strong> waterbody and waterway models should be viewed as only indica<strong>to</strong>rs<br />

<strong>of</strong> <strong>the</strong> nor<strong>the</strong>rn pike population-habitat relationships with <strong>the</strong>ir primary value being <strong>to</strong><br />

improve decision-making in a structured approach. The models are only one aspect <strong>of</strong><br />

identifying <strong>the</strong> risk <strong>of</strong> nor<strong>the</strong>rn pike introductions and should not be relied upon solely <strong>for</strong><br />

decision making.<br />

1. Two ponds ranked high (Towne Pond and Oak Knoll Bog) with each pond being<br />

less than 8 HA in area (20 acres). High ranked waterbodies accounted <strong>for</strong> about<br />

1 percent <strong>of</strong> all <strong>the</strong> lakes and ponds.<br />

2. Ninety-four waterbodies ranked as medium potential and ranged from 2 <strong>to</strong> 582<br />

HA. About 90 percent were less than 40 HA (about 100 acres). The five largest<br />

waterbodies ranked as medium potential include: Endless Lake, Ebeemee Lake,<br />

Burden Pond, Second and Third Branch Ponds, and Shirley Bog. Medium<br />

ranked waterbodies accounted <strong>for</strong> 48 percent <strong>of</strong> all <strong>the</strong> lakes and ponds. Of<br />

<strong>the</strong>se, only Ebeemee and Endless will be accessible. All o<strong>the</strong>rs are above<br />

Sebec Dams (Burden), waterfalls (second and third WB Ponds) or Dover.<br />

3. One hundred waterbodies ranked as low potential and ranged from 2 <strong>to</strong> 2,841<br />

HA. They accounted <strong>for</strong> about 51 percent <strong>of</strong> all <strong>the</strong> lakes and ponds. About 66<br />

percent were less than 40 HA (about 100 acres). The five largest waterbodies<br />

ranked as low potential were: Schoodic Lake, Sebec Lake, Seboeis Lake, Lower<br />

Wilson Pond and Lake Onawa.<br />

PRFP Page 238

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