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Coastal Cutthroat Trout as Sentinels of Lower Mainland Watershed ...

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74Management Strategy 3: Recovery <strong>of</strong> Extirpated <strong>Cutthroat</strong> StocksOf a total <strong>of</strong> 657 known salmonid streams located from Stave River to West Vancouver,120 <strong>of</strong> these have been lost (i.e., in-filled, culverted and/or paved over) during the p<strong>as</strong>t100 years <strong>of</strong> land settlement and urbanization (Precision Identification BiologicalConsultants 1997). Many were significant anadromous cutthroat producers which havebeen reduced to mere remnants such <strong>as</strong> Como Creek in the municipality <strong>of</strong> Coquitlam.Other urban streams remain, but have been degraded with fish access blocked throughpoor culvert installations, and cutthroat trout have been extirpated or partially extirpated,(e.g., extirpation <strong>of</strong> cutthroat upstream <strong>of</strong> Brunette Avenue at Nelson Creek in themunicipality <strong>of</strong> Coquitlam).Although challenging, stocks <strong>of</strong> sea-run cutthroat and access to their habitats can berecovered in many <strong>of</strong> these streams through restoration, contingent upon a strategy b<strong>as</strong>edon public education, public stewardship and municipal involvement that results in:• pollution abatement;• re-establishment <strong>of</strong> native cutthroat by re-stocking juveniles from downstreamreaches or unfed fry cultured from suitable local stocks;• removal <strong>of</strong> culvert barriers by baffles, fishways and culvert replacements; and• establishment <strong>of</strong> stewardship groups to monitor conditions.As soon <strong>as</strong> possible, an <strong>as</strong>sessment and inventory <strong>of</strong> extirpated cutthroat streams andstream reaches needs to be completed for the <strong>Lower</strong> <strong>Mainland</strong> Region. One or twoextirpated systems should be treated <strong>as</strong> pilots or demonstration projects to garner publicinterest and advance the concept <strong>of</strong> cutthroat trout <strong>as</strong> sentinels <strong>of</strong> watershed health. Inaddition, an effort should be made to gain cooperative municipal involvement in therecovery project. Where fe<strong>as</strong>ible and with sufficient public support, sufficient momentummay be attained to “daylight” small sections or reaches <strong>of</strong> streams that have been lost forseveral decades. Strong public interest and support will be the major spin-<strong>of</strong>f <strong>of</strong> thismanagement strategy.Management Strategy 4: <strong>Cutthroat</strong> Nursery Habitat RestorationHabitat restoration may be required if natural processes have been degraded by excessiveflow withdrawals, obstructions, isolation <strong>of</strong> <strong>of</strong>f-channel habitats, curtailed supplies <strong>of</strong>salmon carc<strong>as</strong>ses, and lost or simplified cutthroat summer rearing and over-winteringhabitats. Restoration <strong>of</strong> spawning sites at pool tail-outs is rarely required. A watershedrestoration strategy <strong>of</strong> “best first and worst (most degraded) l<strong>as</strong>t” should be a guidingtheme with cutthroat trout, using benchmark abundances. Early in the planning stages, itmust be recognized that some <strong>of</strong> the more highly degraded urban streams with severelycompromised watershed processes cannot be restored (S. Barrett pers. comm. 2005).Finally, it should be noted that regulatory approvals are required to undertake instreamand <strong>of</strong>f-channel restoration, with binding letters <strong>of</strong> approval required by regulatoryagencies. Documented land holder support is required <strong>as</strong> a condition <strong>of</strong> regulatoryapprovals.

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