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

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Objective 3: Discontinue supplementation in sub-drainages meeting Objective 1<br />

measures (Table 1). S<strong>to</strong>cking should be halted at <strong>the</strong> earliest point possible <strong>to</strong><br />

encourage re-population by wild fish. By year 40, all salmon will be <strong>of</strong> wild origin.<br />

• Evaluate using s<strong>to</strong>cking records/recommendations.<br />

� Strategy- Develop a plan <strong>for</strong> success- how and when <strong>to</strong><br />

s<strong>to</strong>p s<strong>to</strong>cking. This must be peer-reviewed and should<br />

be a central tenet <strong>of</strong> <strong>the</strong> salmon program in Maine.<br />

Constantly assess populations <strong>to</strong> determine if s<strong>to</strong>cking is<br />

warranted under this plan.<br />

� Develop explicit adaptive management plan <strong>to</strong> halt<br />

s<strong>to</strong>cking based on Table 1 measures.<br />

Objective 4: Achieve self-sustaining smolt <strong>to</strong> adult return rates within five years <strong>of</strong> a<br />

sub-drainage achieving 20 % <strong>of</strong> Objective 1 measures <strong>for</strong> hatchery and wild fish<br />

combined (Table 1). Also assess hatchery-derived smolt <strong>to</strong> adult return rates that<br />

could lead <strong>to</strong> self-sustaining populations. Use trapping facilities <strong>to</strong> assess smolt <strong>to</strong><br />

adult return rates.<br />

• Measure 4a: Estimate required return rates <strong>for</strong> self-sustaining<br />

population annually based on population data and PVA model.<br />

� Strategy- use modeling <strong>to</strong> set targets with uncertainty. Test<br />

models against empirical data as <strong>the</strong>y become available.<br />

Adjust models as needed <strong>to</strong> improve target(s).<br />

• Measure 4b: Return rates based on marked groups at Veazie and/or<br />

Mil<strong>for</strong>d<br />

� Strategy- s<strong>to</strong>ck marked smolts and set up proper sampling<br />

scheme <strong>to</strong> assess return rates <strong>of</strong> hatchery fish. Compare <strong>to</strong><br />

wild. Adapt as necessary <strong>to</strong> improve. Change rearing<br />

regime/environment, s<strong>to</strong>cking methods (timing etc.).<br />

• Measure 4c: Naturally reared return rates<br />

� Strategy- Estimate natural return rates via juvenile or smolt<br />

assessments and returning adult census (trap or redd<br />

counts). Use data from un-dammed rivers <strong>to</strong> augment our<br />

understanding. Test against rates needed <strong>for</strong> recovery. Use<br />

in<strong>for</strong>mation <strong>to</strong> address habitat/environment issues.<br />

• Measure 4d: Smolt <strong>to</strong> adult return rates (SAR)<br />

o S<strong>to</strong>cked above one dam<br />

o SAR based on s<strong>to</strong>cking location<br />

� Strategy- Assess smolt return rates in relation <strong>to</strong> s<strong>to</strong>cking<br />

location and dams. Identify opportunities (promising return<br />

rates) and problems (return rates that are unlikely <strong>to</strong> yield<br />

recovery). Aggressively pursue proactive management in<br />

promising areas and identify limiting fac<strong>to</strong>rs in problem<br />

areas. Shift resources away from problem areas until<br />

limiting fac<strong>to</strong>rs have been addressed.<br />

• Measure 4e: Number <strong>of</strong> returns <strong>to</strong> Weldon as a proportion <strong>of</strong> what is<br />

s<strong>to</strong>cked upstream.<br />

PRFP Page 183

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