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

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During <strong>the</strong> development <strong>of</strong> <strong>the</strong> <strong>Operational</strong> <strong>Plan</strong>, DMR considered <strong>the</strong> likely success<br />

<strong>of</strong> passive (natural recolonization) versus active (s<strong>to</strong>cking) shad res<strong>to</strong>ration. In<br />

practice <strong>the</strong>re are no examples <strong>of</strong> American shad populations in large rivers that<br />

have been res<strong>to</strong>red or are being res<strong>to</strong>red solely by natural recolonization.<br />

<strong>Res<strong>to</strong>ration</strong> programs in Maine, New Hampshire, Massachusetts, Rhode Island,<br />

Virginia, Maryland and Pennsylvania have relied on s<strong>to</strong>cking adults, juveniles, or fry<br />

<strong>to</strong> increase <strong>the</strong> abundance <strong>of</strong> shad. However, <strong>the</strong>re are two examples in Maine<br />

where natural recolonization has resulted in a static shad population. On <strong>the</strong> Saco<br />

River where adult shad have simply been passed upriver <strong>the</strong> average run size <strong>for</strong> 16<br />

years is 1435 fish. On <strong>the</strong> Narraguagus River, counts <strong>of</strong> adult shad passing <strong>the</strong><br />

single nonhydropower dam in each <strong>of</strong> three years (1987, 1989, 2007) have never<br />

exceeded 200 fish.<br />

DMR developed two models <strong>to</strong> explore scenarios that were likely <strong>to</strong> achieve shad<br />

res<strong>to</strong>ration <strong>to</strong> estimated his<strong>to</strong>rical abundance in <strong>the</strong> 40-50 year time frame <strong>of</strong> this<br />

<strong>Operational</strong> <strong>Plan</strong> (8-10 shad generations). These models are simple, because <strong>the</strong>re<br />

is a paucity <strong>of</strong> demographic data <strong>for</strong> shad populations in Maine as well as <strong>for</strong> shad<br />

populations along <strong>the</strong> Atlantic coast.<br />

The first model explored <strong>the</strong> possibility <strong>of</strong> achieving <strong>the</strong> res<strong>to</strong>ration objective by<br />

natural recolonization; it uses a range <strong>of</strong> starting population sizes and intrinsic rates<br />

<strong>of</strong> increase from one generation <strong>to</strong> <strong>the</strong> next (Table 5). The model indicates that<br />

achieving Measure 7.1 (633,300 adult shad returns in 41-50 years) by natural<br />

recolonization would require ei<strong>the</strong>r a very high rate <strong>of</strong> increase <strong>for</strong> a prolonged<br />

period or a very large starting population. For example, this target could be reached<br />

with a starting population <strong>of</strong> 2500-5000 fish that on average doubled in abundance<br />

every five years. This level <strong>of</strong> reproduction might be expected in bacteria, but not in<br />

shad. If <strong>the</strong> rate <strong>of</strong> reproduction is reduced <strong>to</strong> 1.5 or 1.25, <strong>the</strong> size <strong>of</strong> <strong>the</strong> starting<br />

population would have <strong>to</strong> be 40,000 <strong>to</strong> 135,000 fish. DMR is not aware <strong>of</strong> shad<br />

populations in Maine or elsewhere that consistently achieve <strong>the</strong>se levels <strong>of</strong><br />

reproduction nor <strong>of</strong> remnant populations on <strong>the</strong> east coast that have been greater<br />

than about 1000 fish. DMR has concluded that reliance on natural recolonization is<br />

not a valid management strategy.<br />

PRFP Page 22

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