Table 5.
H origin | Artificial selection? | Program | Hatchery gens.a | Species | Trait | Change | Other comments and/or caveats | Reference |
---|---|---|---|---|---|---|---|---|
Local | No | S | 1 | Chinook salmon | Predator avoidance | H<W | 2.2% reduction in survival | Fritts et al. (2007) |
Localb | No | S/H | 4–7 | Rainbow trout | Predator avoidance | H<W | 16.3–28.9% reduction in survival | Berejikian (1995) |
Local | No | S/H | 5 | Brown trout | Antipredator response | H<W | Ferno and Jarvi (1998) | |
Local | No | S/H | >5c | Brown trout | Antipredator response | H<W | Johnsson et al. (1996) | |
Local | No | S | 1 | Chinook salmon | Aggression | 0 | Large number of comparisons (n = 97 to 276, depending on the type of competition) | Pearsons et al. (2007) |
Local | No | S/H | >5c | Brown trout | Aggression | 0 | Large number of comparisons (n = 287) | Johnsson et al. (1996) |
Localb | No | S/H | 4–7 | Rainbow trout | Aggression | H> <Wd | Berejikian et al. (1996) | |
Local | No | S/H | >5c | Brown trout | Juvenile growth rate | H>W | Johnsson et al. (1996) | |
Local | No | S | 0 | Rainbow trout | Length/weight | H>W | Not reared under common conditions | Kostow (2004) |
Variance in length/weight | H<W | Not reared under common conditions | ||||||
Variance in age | H<W | Not reared under common conditions | ||||||
Local | No | S | 4–6e | Chinook salmon | Female egg size | H<W | Egg size reduction in two populations with considerable supplementation (28–43%); no change in egg size in two other populations with low supplementation (4–16%) | Heath et al. (2003) |
Genetic effects were not disentangled from environmental effects on egg size | (see Beacham 2003; Fleming et al. 2003) | |||||||
Local | No | S | 1 | Brown trout | Juvenile growth rate | H>W | Differences were small | Dahl et al. (2006) |
Local | No | S/H | <1f | Brown trout | Antipredator response | H<W | Not reared under common conditions | Dellefors and Johnsson (1995) |
Local | No | S/H | >25g | Coho salmon | Aggression | H>W | Not reared under common conditions | Rhodes and Quinn (1998) |
Local | Yes | H | >10h | Brook trout | Juvenile growth rate | H>W | Hatchery fish were selected for growth | Vincent (1960) |
Local | Yes | H | >10h | Brook trout | Wariness | H<W | Hatchery fish were selected for growth | Vincent (1960) |
Locali | Yes | F | 5–7 | Atlantic salmon | Antipredator response | H<W | Hatchery fish were farmed | Johnsson et al. (2001) |
Local | Yes | F | 1 | Atlantic salmon | Body morphology | H≠W | Hatchery fish were farmed | Fleming et al. (1994) |
Nonlocal | No | S | 4–5j | Coho salmon | Body morphology | H≠W | Hatchery fish: smaller heads, more streamlined bodies Different ancestral origin of hatchery fish | Swain et al. (1991) |
Nonlocal | No | S | 2–3k | Rainbow trout | Adult body size | H>W | Inadvertent selection of larger body size | McLean et al. (2005) |
Nonlocal | No | S | 2–3k | Rainbow trout | Adult run-timing | H≠W | Inadvertent selection of earlier-run timing females for fulfilling hatchery recruitment requirements | McLean et al. (2005) |
Nonlocal | No | S | ? | Atlantic salmon | Juvenile growth rate | H>W | Kallio-Nyberg and Koljonen (1997) | |
Nonlocal | No | S | 4–5j | Coho salmon | Aggression | H>W | Swain and Riddell (1990) | |
Nonlocal | No | H | ? | Atlantic salmon | Aggression | H<W | Norman (1987) | |
Nonlocal | No | H | ? | Brook trout | Aggression | H>W | Moyle (1969) | |
Nonlocal | No | S/H | 1–2 | Brown trout | Antipredator response | H<W | Not reared under common conditions | Alvarez and Nicieza (2003) |
Nonlocal | No | S/H | 1 | Coho salmon | Male spawning performance | H<W | Not reared under common conditions | Fleming and Gross (1993) |
Nonlocal | No | S | ? | Chinook salmon | Male spawning performance | H<W | Not reared under common conditions | Chebanov and Riddell (1998) |
Nonlocal | No | S | ? | Chinook salmon | Female spawning performance | H<W | Not reared under common conditions | Chebanov and Riddell (1998) |
Nonlocal | Yes | F | 5–7 | Atlantic salmon | Male spawning performance | H<W | Not reared under common conditions | Fleming et al. (2000) |
Nonlocal | Yes | S/H | >5 | Rainbow trout | Antipredator response | H<W | Hatchery fish were selected for growth | Johnsson and Abrahams (1991) |
Nonlocal | Yes | S | >15l | Masu salmon | Antipredator response | H<W | Chemically simulated predator attack | Yamamoto and Reinhardt (2003) |
Nonlocal | Yes | F | 5–7 | Atlantic salmon | Antipredator response | H<W | Hatchery fish were farmed | Einum and Fleming (1997) |
Nonlocal | Yes | F | 5–7 | Atlantic salmon | Antipredator response | H<W | Hatchery fish were farmed | Fleming and Einum (1997) |
Nonlocal | Yes | F | 4–7 | Atlantic salmon | Juvenile growth rate | H>W | Hatchery fish were farmed | McGinnity et al. (2003) |
Nonlocal | Yes | S | >15l | Masu salmon | Juvenile growth rate | H>W | Hatchery fish were selected for growth | Yamamoto and Reinhardt (2003) |
Nonlocal | Yes | S | >15l | Masu salmon | Aggression | 0 | Hatchery fish were selected for growth | Yamamoto and Reinhardt (2003) |
Hatchery and wild populations were compared under common environmental conditions, unless otherwise noted. Statistical significance was based on P < 0.05, unless otherwise noted.
Program type: S, supplementation; C, captive-breeding; H, harvest augmentation; F, farmed/aquaculture. H<W, hatchery population showed reduced aggression/antipredator response/predator avoidance/growth rate/egg size etc. relative to the wild population; H>W, hatchery population showed greater aggression/antipredator response/predator avoidance/growth rate/egg size etc. relative to the wild population; H≠W, hatchery population shifted in other traits from the wild population (details of the main shifts provided); 0, no change observed; ?, not presented or with insufficient detail.
Hatchery generations refer to the number of generations in which the hatchery program involving a local or nonlocal hatchery population had taken place at the time the study was conducted. Note, however, that the hatchery programs themselves might differ. In some cases, naturally-spawning adults are collected from the wild; their offspring are raised in hatcheries for a period of time and then released back into the wild. In other cases, particularly traditional hatchery programs, hatchery fish are regenerated from captive broodstock that were maintained solely in hatcheries. Particularly for older hatchery programs (i.e., more generations), details regarding whether the latter was involved were not always clear.
Hatchery population originated from a wild population that was very geographically close to the wild population used in comparisons. The authors acknowledge that the existence of genetically distinct subpopulations within the same drainage system might have been a confounding effect for their comparison of hatchery and wild steelhead (Berejikian 1995; Berejikian et al. 1996)
Based on a generation time of 3.8 years for anadromous brown trout.
Direction of change depended on age. Newly emergent fry: H<W; 105 days postemergence: H>W.
Based on a generation time of 3.0 years for Chinook salmon.
Not stated in the article how long hatchery fish have been generated for this river. However, in this study, the important aspect was the comparison between some fish born and reared in the hatchery and those that had wild exposure for the first 1+ year of life (see Dellefors and Johnsson 1995).
Based on 100 years of hatchery propagation on the same wild population.
Based on a generation time of 3.0 years for brook trout.
Authors acknowledge that the farmed strain was derived principally from the same wild population where comparisons were being made.
Hatchery populations had been established for four to five generations for five of six hatchery populations, and two generations in one case.
Based on a generation time of 3.0 years for anadromous steelhead.
Based on a 2-year generation time for this masu salmon population (Yamamoto and Reinhardt 2003).