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

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We estimated cumulative dam mortalities <strong>for</strong> each migra<strong>to</strong>ry route <strong>for</strong> both smolts<br />

and adults. For smolts we used data from Holbrook (2007) that estimated <strong>the</strong><br />

proportion <strong>of</strong> smolts choosing <strong>to</strong> migrate down <strong>the</strong> mainstem Penobscot as opposed<br />

<strong>to</strong> using <strong>the</strong> Stillwater Branch. We <strong>the</strong>n used <strong>the</strong>se cumulative mortalities <strong>to</strong><br />

calculate life stage specific monthly survivals and applied this additional monthly<br />

mortality <strong>to</strong> life stage specific monthly mortalities. These survivals were <strong>the</strong>n used<br />

as parameters in a population matrix model (Robertson 2005, Sweka 2008) that<br />

estimated <strong>the</strong> population growth rate (lambda) as well as projected population size.<br />

We <strong>the</strong>n compared <strong>the</strong>se results <strong>to</strong> a reach without dam-related mortality. We did<br />

not consider amount or productivity <strong>of</strong> rearing habitat in <strong>the</strong> reaches, although we<br />

present data from Rago (1986) that do. The purpose <strong>of</strong> this exercise was <strong>to</strong><br />

evaluate <strong>the</strong> effect <strong>of</strong> dams on <strong>the</strong> population dynamics <strong>of</strong> <strong>the</strong> sub-populations. We<br />

also ran scenarios under optimistic marine survival conditions, where marine survival<br />

was set in <strong>the</strong> model <strong>to</strong> obtain a stable population (lambda = 1), and <strong>the</strong>n damrelated<br />

mortality was inflicted on <strong>the</strong> population. This allowed us <strong>to</strong> estimate <strong>the</strong><br />

affects <strong>of</strong> <strong>the</strong> dams under ocean conditions that should o<strong>the</strong>rwise allow viable subpopulations.<br />

The cumulative effect <strong>of</strong> dam mortality varied across management reaches in <strong>the</strong><br />

Penobscot basin be<strong>for</strong>e and after <strong>the</strong> Penobscot Project dam removal and bypass<br />

(referred <strong>to</strong> as “dam removal” from here on) (Figure 1). We assumed that <strong>the</strong><br />

Howland bypass will be as effective as dam removal, and set dam related mortality<br />

<strong>to</strong> zero <strong>for</strong> this site after dam removal. Kenduskeag Stream represents a reference<br />

state with no dams, while <strong>the</strong> o<strong>the</strong>r reaches have varying numbers <strong>of</strong> dams,<br />

increasing with upstream distance. Note that some reaches improve more than<br />

o<strong>the</strong>rs with dam removal, particularly <strong>the</strong> Lower and Upper Piscataquis. However,<br />

all values <strong>of</strong> lambda are well below one, indicating that all sub-populations are not<br />

viable under current ocean survival conditions.<br />

PRFP Page 135

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