Thanks,
I also found two more articles.
The first one has nothing to do with my firsts questions but it may interest some people... It is about the impact of catch and release on the Vedder and I see that Chris is thanked at the end of the manuscript.
Behavior and Survival of Wild and Hatchery-Origin Winter
Steelhead Spawners Caught and Released in a
Recreational Fishery
T. C. NELSON et al.
North American Journal of Fisheries Management 25:931–943, 2005
Abstract.—Mandatory catch and release of wild fish and supplementation with hatchery-reared
fish are commonly used to sustain sport fisheries on low-abundance populations of wild steelhead.
However, their effectiveness in limiting angling mortality on wild fish is uncertain. We radiotagged
226 (125 wild, 101 hatchery) angled adult steelhead Oncorhynchus mykiss near the mouth
of the Vedder2Chilliwack River, British Columbia, in 1999 and 2000 and monitored their subsequent
movements to determine survival to spawning and overlap in the distributions of inferred
holding sites, spawning sites, and spawning times. The distributions of prespawning holding sites
did not differ between wild and hatchery fish in either year, but spawning locations differed.
Holding and spawning sites used by hatchery fish were restricted to the lower two-thirds of the
river, downstream of the hatchery where they were reared but well upstream of their smolt release
site. Wild fish spawned throughout the watershed. Spawning times did not differ between wild
and hatchery fish, but varied with run timing. The maximum mortality from the initial catch and
release and radio-tagging was 1.4% in 1999 and 5.8% in 2000; true mortality rates were lower
because tag regurgitation was indistinguishable from death. The fishery subsequently killed 2.5%
of tagged wild fish and harvested 20% (1999) and 43% (2000) of the hatchery fish. Seventy-two
tagged fish were recaptured and released in the sport fishery up to three times without any mortality
before spawning. Hatchery fish were recaptured at twice the rate of wild fish. At least 92% of
unharvested fish spawned, and 75% of successful spawners survived to emigrate from the watershed.
The incidence of postspawning death did not vary with the frequency of capture and release.
Catch-and-release angling imposed small costs in terms of survival; however, behavioral differences
existed between adult wild fish and the adult F1 progeny of wild fish reared to smolt stage
in a hatchery.
The second one seems to indicate that there are a lot of crosses between resident rainbow and steelheads, but I am not completely convinced by this one
Evidence of partial anadromy and resident-form dispersal bias on a fine scale
in populations of Oncorhynchus mykiss
Jeffrey B. Olsen et al.
Conservation Genetics (2006) 7:613–619
Abstract
We examine sympatric anadromous (steelhead) and nonanadromous (resident) rainbow trout
(Oncorhynchus mykiss) from neighboring locations to test three hypotheses: (1) the sympatric life history
types are not genetically different; (2) fine-scale dispersal is the same for both sexes, and (3) fine-scale
dispersal is the same for steelhead and resident individuals. Data from 13 microsatellite loci reveal no
genetic difference between sympatric steelhead and resident O. mykiss but moderate population structure
(FST=0.019–0.028) between adjacent samples, regardless of life history type. Our results provide further
evidence of partial anadromy and suggest that geographic proximity and genetic history, more than
migratory type, should be considered when identifying populations for use in restoration of local genetic
diversity. We find evidence of resident-form dispersal bias on a fine spatial scale, however, we find no
evidence that fine-scale dispersal varies by gender. Conservation strategies should aim to maintain resident
and anadromous forms when they occur in sympatry, as they may be important in facilitating gene flow on
small and large spatial scales, respectively.
ps: It is crazy, the more I write in English, the more I feel like I do a lot of mistakes