82• Refinement <strong>of</strong> the minimum size regulation <strong>of</strong> 30 cm in freshwater (i.e., north <strong>of</strong>Jervis Inlet) to ensure a minimum <strong>of</strong> a first-time spawning by sea-run (or riverrun)cutthroat trout is advised. Facilitation <strong>of</strong> first-time spawning is a soundconservation me<strong>as</strong>ure which may require a 33-35 cm minimum size <strong>as</strong> in someUS jurisdictions (Gresswell and Harding 1997).Anadromous <strong>Cutthroat</strong> Stream Stocking Program:• Stocking <strong>of</strong> hatchery smolts (or fingerlings) in nursery streams should becarefully managed to minimize risks to wild stocks and wild-hatchery interactions(see research needs, under Management Strategy 5);Smolt stocking should be restricted to designated “hatchery rivers” and at 1-2sites in the Fr<strong>as</strong>er mainstem. Perhaps the lower Alouette River should also bedesignated <strong>as</strong> a hatchery cutthroat river, considering its 25 year stocking history,subject to monitoring wild-hatchery interactions in this watershed. Yet, habitatrestoration and unfed cultured fry stocking <strong>of</strong> nursery streams is a soundalternative to incre<strong>as</strong>e wild cutthroat production, which w<strong>as</strong> recommended forAlouette River tributaries by DeLeeuw and Stuart (1980). Prior to the hatcheryprogram in the fall-winter fishery <strong>of</strong> 1979, only 37 wild cutthroat were caught in4,600 hours <strong>of</strong> angling at the Alouette River (DeLeeuw 1981); thus, anglingpressure w<strong>as</strong> very high, and in part incidental to the steelhead fishery.As an alternative intensive fishery, serious consideration should be given toadding <strong>Lower</strong> Capilano River <strong>as</strong> a “hatchery cutthroat stream” using a captiveBrothers Creek stock. The Capilano w<strong>as</strong> rated <strong>as</strong> “the most popular <strong>of</strong> all riversfor cutthroat fishing in the <strong>Lower</strong> <strong>Mainland</strong>” (DeLeeuw and Stuart 1981). Thelower Capilano River h<strong>as</strong> a highly manipulated hydrology, <strong>as</strong> well <strong>as</strong> hatcherysupportedsalmon and steelhead. These are highly unlikely to be altered, and thusthere are minimal risks to wild fish from a significant cutthroat stocking. Further,there is little conflict with steelhead if cutthroat stocking is restricted to the lowernon-canyon reach <strong>of</strong> the Capilano River.• Optimal smolt size at rele<strong>as</strong>e needs refinement because the average smolt size iscurrently small (17-18 cm) compared to a more optimal size <strong>of</strong> 20 cm (Figure 8).However, a trade<strong>of</strong>f is evident with a high percent residualism <strong>of</strong> large smolts <strong>as</strong>w<strong>as</strong> documented earlier from an experimental stocking <strong>of</strong> 112 g cutthroat smoltsin the Little Campbell River (38 %; Rempel et al. 1984). Furthermore, small (60g, 17 cm) sized smolts stocked within a “hatchery stream” is counter productivebecause only 5 % <strong>of</strong> about 5,000 cutthroat caught were harvested at Stave Riverin the year-round 1993 sport fishery. Thus, larger 20-22 cm smolts should beconsidered for Stave River, thus providing a higher quality catch and harvestalong with much greater returns <strong>of</strong> large sea-run cutthroat. Experimental rele<strong>as</strong>es<strong>of</strong> two size groups at Stave River should be used to evaluate optimal smolt size atrele<strong>as</strong>e, using underwater (snorkel) counts and spot creel checks <strong>of</strong> the catch rateand composition <strong>of</strong> cutthroat trout. Similarly, the Capilano River would be
83another prime target for rele<strong>as</strong>e <strong>of</strong> large sea-run cutthroat smolts <strong>as</strong> discussedearlier.<strong>Co<strong>as</strong>tal</strong> <strong>Cutthroat</strong> Lake Fisheries:• Lake cutthroat fisheries at wild stock lakes in the <strong>Lower</strong> <strong>Mainland</strong> Region shouldemph<strong>as</strong>is selective nursery stream restoration to recover historical parrrecruitment capacities to improve catch success for co<strong>as</strong>tal cutthroat trout. Toimprove angling quality, maximum size regulations should be implemented atsome <strong>of</strong> the more productive wild cutthroat lakes capable <strong>of</strong> growing largepiscivorous cutthroat (e.g., Ruby Lake on the Sunshine Co<strong>as</strong>t <strong>as</strong> a primeexample). Similarly, at hatchery supported cutthroat or cutthroat-rainbow lakes,innovative use and evaluation <strong>of</strong> piscivorous sterile (triploid) cutthroat is worthevaluating further and expanding where appropriate to improve fishing quality.