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Biological Opinions - Bureau of Reclamation

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survey records until the 1900’s, it is likely that these once superabundant species began to<br />

decline in numbers around the turn <strong>of</strong> the 20 th century concurrent with significant destruction and<br />

degradation <strong>of</strong> sucker habitat. Later, from the 1960s to the early 1980s, recreational harvests <strong>of</strong><br />

suckers in UKL progressively decreased (Markle and Cooperman 2002), which reflected further<br />

declines in the LRS and SNS populations and led to their listing under the ESA in 1988. From<br />

1995 to 1997, water quality-related die-<strong>of</strong>fs killed thousands <strong>of</strong> adult suckers in UKL (Perkins et<br />

al. 2000b). Over that three-year period, more than 7,000 dead suckers were collected and many<br />

other dead suckers were likely present but not detected.<br />

More recently (between 2002 and 2010), the abundance <strong>of</strong> LRS males in the lakeshore-spawning<br />

subpopulation in UKL decreased by 50 to 60 percent, and the abundance <strong>of</strong> females in UKL<br />

decreased by 29 to 44 percent (Hewitt et al. 2012; Figure 7.2). It is not clear if the riverspawning<br />

subpopulation <strong>of</strong> the LRS in UKL has increased or decreased between 2002 and 2010<br />

because <strong>of</strong> improvements in sampling methodology part way through the study that give the<br />

appearance <strong>of</strong> a large influx <strong>of</strong> individuals, but it is likely that this population decreased<br />

proportionately similar to the spring-spawning population (Hewitt et al. 2012).<br />

Capture-recapture data indicate that the UKL SNS adult population decreased in abundance by<br />

64 to 82 percent for males and 62 to 76 percent for females between 2001 and 2010 (Hewitt et al.<br />

2012). Although the adult populations <strong>of</strong> both species in UKL have declined substantially, the<br />

SNS adult population is at a greater risk <strong>of</strong> extirpation from UKL than LRS because it had<br />

declined to a greater degree and there are approximately 10 times LRS in UKL than SNS (Hewitt<br />

et al. 2012). If the trend from 2001 through 2010 continues for the SNS in UKL we may expect<br />

that roughly 1,000 will remain by the end <strong>of</strong> the term <strong>of</strong> the BiOp in this water body. However,<br />

the risk <strong>of</strong> extirpation becomes even more likely given that the relatively advanced age <strong>of</strong> most<br />

individuals in UKL will likely result in an acceleration <strong>of</strong> declining trends during the BiOp term<br />

as individuals begin to succumb to old age.<br />

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