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Biological Opinions - Bureau of Reclamation

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By late July, surviving larval suckers have metamorphosed into age-0 juveniles. Water quality<br />

has become highly dynamic, with wide daily swings in DO, pH, and total ammonia, which cause<br />

stress in the fish. Water temperatures peak at this time, reducing the capacity <strong>of</strong> the water to<br />

hold DO in solution. Higher temperatures also raise energy demands <strong>of</strong> fish, thus adding stress.<br />

Cyanotoxins can also be present at this time and, when concentrations are high, they damage the<br />

gut and liver, impacting the health <strong>of</strong> the fish, and leading to stress or mortality. Parasites,<br />

including protozoans like Tricodina, the copepod Lernaea, and the trematode Neascus, are also<br />

attacking the juveniles, adding additional stress and mortality. When fish are highly stressed and<br />

water temperatures high, protozoan parasites can multiply quickly, causing death in a few days.<br />

Additionally, in August and September, lake levels are declining and preferred habitats where<br />

food might be most abundant are disappearing, perhaps causing the juveniles suckers to relocate<br />

to areas where food might be less abundant. This movement also expends energy and further<br />

stresses the fish, and could increase their exposure to predators, especially fish-eating birds. Of<br />

those juveniles that survive, many end up at the south end <strong>of</strong> the lake and are entrained at the<br />

Link River Dam or in the forebay <strong>of</strong> the A Canal. Consequently, by early fall, very few<br />

juveniles survive in most years to enter the adult population 4 to 7 years later.<br />

Table 7.9 Threats to the LRS and the SNS in UKL.<br />

Threat<br />

Entrainment at<br />

Link River<br />

Nature <strong>of</strong><br />

Threat<br />

Mortality and<br />

loss from<br />

population<br />

Life Stage<br />

Affected<br />

Mostly affects<br />

larvae and age-0<br />

juveniles<br />

Primary Effect<br />

Studies show<br />

this occurs<br />

annually, but<br />

extent varies<br />

among years<br />

Mitigating<br />

Factor(s)<br />

Will only<br />

affect larvae<br />

and juveniles at<br />

south end <strong>of</strong><br />

UKL<br />

References<br />

Gutermuth et<br />

al. 2000a, b<br />

Low<br />

Dissolved<br />

Oxygen<br />

Concentrations<br />

High Total<br />

Ammonia<br />

Concentrations<br />

Mortality or<br />

stress and<br />

reduced<br />

productivity<br />

Mortality or<br />

stress and<br />

reduced<br />

productivity<br />

Juveniles and<br />

adults mostly<br />

due to timing<br />

Juveniles and<br />

adults mostly<br />

due to timing<br />

98<br />

Good evidence<br />

that this led to<br />

die-<strong>of</strong>fs in<br />

1990s<br />

New analyses<br />

show water<br />

quality exceeds<br />

LC 50 values<br />

more than any<br />

other parameter<br />

Lethal<br />

conditions are<br />

variable in time<br />

and space and<br />

are unlikely to<br />

cover large<br />

areas <strong>of</strong> the<br />

lake;<br />

fish should be<br />

able to avoid<br />

affected areas<br />

to some degree<br />

Lethal<br />

conditions are<br />

variable in time<br />

and space and<br />

are unlikely to<br />

cover large<br />

areas <strong>of</strong> the<br />

lake;<br />

fish should be<br />

Perkins et al.<br />

2000b<br />

B. Martin,<br />

USGS, pers.<br />

comm., 2012

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