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Feasibility of Fish Passage at Alameda Creek Diversion Dam

Feasibility of Fish Passage at Alameda Creek Diversion Dam

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8.0 Conclusion8 CONCLUSIONThis technical memorandum identifies conceptual-level fish passage options <strong>at</strong> ACDD and assessesthe feasibility <strong>of</strong> implementing passage to benefit steelhead when popul<strong>at</strong>ions are restored to the<strong>Alameda</strong> <strong>Creek</strong> W<strong>at</strong>ershed. The analysis finds th<strong>at</strong> a fish ladder combined with install<strong>at</strong>ion <strong>of</strong>screens is a technologically feasible option for providing volitional passage for steelhead <strong>at</strong> ACDD.This analysis finds a fish ladder around ACDD on the right bank <strong>of</strong> <strong>Alameda</strong> <strong>Creek</strong>, in conjunctionwith implementing screens <strong>at</strong> ACDT and fish screen bypass flows on the left side <strong>of</strong> the dam to be themost feasible method for providing volitional passage (ACDD <strong>Fish</strong> Ladder Option, Section 7.1). Theperformance <strong>of</strong> a fish ladder would depend upon passage conditions for immigr<strong>at</strong>ing steelhead in theLittle Yosemite reach <strong>of</strong> <strong>Alameda</strong> <strong>Creek</strong> (see Sections 2.3.1 and 6.1). If Little Yosemite significantlylimits immigr<strong>at</strong>ing steelhead from reaching a fish ladder <strong>at</strong> ACDD, trap and haul from below LittleYosemite to above ACDD (Ohlone Trap and Haul Option, Section 7.2) could also provide passage,although long-term success <strong>of</strong> such passage would depend on ongoing institutional commitment andfunding. Screening and fish screen bypass flows to protect steelhead from entrainment in the ACDTwould be required with any type <strong>of</strong> fish passage and bypass flows would provide safe downstreampassage for emigr<strong>at</strong>ing steelhead.The estim<strong>at</strong>ed total capital cost <strong>of</strong> components associ<strong>at</strong>ed with a fish ladder passage option and a trapand haul passage option are <strong>of</strong> a similar order <strong>of</strong> magnitude ($23.7 and $21.7 million, respectively), inboth cases more than half <strong>of</strong> which is the estim<strong>at</strong>ed cost <strong>of</strong> fish screens <strong>at</strong> the ACDT (Section 5.1).Including estim<strong>at</strong>ed w<strong>at</strong>er costs, the order-<strong>of</strong>-magnitude capital and oper<strong>at</strong>ing and maintenance costfor fish passage with screening <strong>at</strong> ACDD, annualized over a period <strong>of</strong> 30 years, is estim<strong>at</strong>ed <strong>at</strong>approxim<strong>at</strong>ely $4 million annually for either a fish ladder or trap and haul passage option. In bothcases, more than $3 million <strong>of</strong> the estim<strong>at</strong>ed annual cost is associ<strong>at</strong>ed with screens. A significantportion <strong>of</strong> the annual cost <strong>of</strong> passage <strong>at</strong> the ACDD is estim<strong>at</strong>ed to be lost w<strong>at</strong>er diversion opportunity(Section 5.2).Facilit<strong>at</strong>ing steelhead passage <strong>at</strong> ACDD would provide access to likely suitable steelhead spawningand juvenile rearing habit<strong>at</strong> above the diversion dam, and specific engineering solutions to providepassage are technologically feasible. Based on the limited detailed d<strong>at</strong>a available regarding habit<strong>at</strong>conditions in the Upper <strong>Alameda</strong> <strong>Creek</strong> Basin (see Section 6.1), it is unknown whether habit<strong>at</strong> aboveACDD is sufficient to support a self-sustaining popul<strong>at</strong>ion once steelhead gain passage <strong>at</strong> the BARTweir and re-enter the Upper <strong>Alameda</strong> <strong>Creek</strong> Basin. If habit<strong>at</strong> is not sufficient to support a selfsustainingpopul<strong>at</strong>ion above ACDD, provision <strong>of</strong> passage could still contribute to a steelheadmetapopul<strong>at</strong>ion in the <strong>Alameda</strong> <strong>Creek</strong> W<strong>at</strong>ershed, if additional subpopul<strong>at</strong>ions are established in otherreaches. Detailed surveys <strong>of</strong> potential steelhead habit<strong>at</strong> above ACDD, in cooper<strong>at</strong>ion with upstreamlandowners, would allow for a more accur<strong>at</strong>e assessment <strong>of</strong> the potential biological benefit <strong>of</strong>steelhead passage <strong>at</strong> ACDD.The volitional passage option <strong>of</strong> a fish ladder is generally preferred compared to non-volitionaloptions such as trap and haul. However, it is currently not known definitively whether adequ<strong>at</strong>enumbers <strong>of</strong> immigr<strong>at</strong>ing steelhead would be able to reach the ACDD if a fish ladder was constructed.Given the substantial costs potentially associ<strong>at</strong>ed with either passage option (see Section 5), and theuncertainty <strong>of</strong> passage conditions <strong>at</strong> Little Yosemite, it is important to understand which option wouldprovide the gre<strong>at</strong>est benefit to the species. When steelhead return to the base <strong>of</strong> Little Yosemite, itwill be possible to observe and directly evalu<strong>at</strong>e passage <strong>at</strong> this fe<strong>at</strong>ure. The results <strong>of</strong> theseobserv<strong>at</strong>ions could be used to refine analysis regarding providing immigr<strong>at</strong>ion passage for steelhead<strong>at</strong> ACDD.ACDD <strong>Passage</strong> June 2009 Page 8-1

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