Oncorhynchus mykiss
rainbow trout
Type Locality
Columbia River at Fort
Vancouver, Vancouver, Washington (Richardson 1836).
Etymology/Derivation of Scientific Name
Oncorhynchus: hooked
snout; mykiss a vernacular name for the species in Kamchatka, Russia
(Ross 2001).
Synonymy
Salmo gaidnerii
Richardson 1836:221.
Characters
Maximum size: 1000 mm
TL (Behnke 1980).
Coloration: paired
fins with white border; small spots heavily scattered along sides and caudle
fin (Hubbs et al 1991).
Counts: 120-140
lateral scale rows (Hubbs et al 1991). There are 100-150 SC, 16-22
gillrakers, 10-12 dorsal rays, 10-11 (8-13) anal rays, 11-17 pectoral rays,
and 9-10 pelvic rays (Ross 2001; modified from Scott and Crossman 1973;
Robison and Buchanan 1988).
Body shape: Elongate,
laterally compressed fish (Ross 2001).
Mouth position:
Terminal (Goldstein and Simon 1999). Teeth present on jaws, palantine bones
in roof of mouth and tip of tongue; no teeth present on midline of tongue
(Robison and Buchanan 1988).
External morphology:
Has a single, spineless dorsal fin and an adipose fin. The maxillary seldom
extends posteriorly beyond the eye. Small axillary processes are present at
the base of the pelvic fins; lateral line is complete (Ross 2001). Breeding
males develop a hook on lower jaw (Robison and Buchanan 1988).
Distribution (Native and Introduced)
U.S. distribution:
Native to streams of the Pacific Northwest from Baja, California to Alaska (Hubbs
et al 1991).
Texas distribution:
This introduced species has a self-sustaining population only in McKittrick
Canyon in the Guadalupe Mountains; introduced individuals may be found in
many other localities that provide a “put and take” fishery (Knapp1953;
Hubbs et al 1991). Sam Rayburn Reservoir (impounds the Angelina River;
Anderson et al. 2002). Texas Parks and Wildlife (2001) lists species records
for the following locations: (Data courtesy of the U.S. Geological Survey –
USGS home page http://www.usgs.gov).
TX - Buffalo Wallow Pond
TX - Burke-Crenshaw Lake [near Pasadena]
TX - Cy Miller Pond
TX - Guadalupe River
TX - Hereford City Lake
TX - Meredith Reservoir
TX - Meredith Stilling Basin [below Lake Meredith]
TX - Meridian State Park Lake
TX - Pedernales River
TX - Placid Reservoir, near San Antonio
TX - Plum Lake
TX - Purtis Creek State Park, lake, northeast Texas
TX - Rheudasil Lake [community fishing lake in Flower Mound, TX]
TX - Travis Reservoir
TX - Waterloo Reservoir
TX - San Antonio River
TX - Carrollton Sports Complex Lake
Abundance/Conservation status (Federal, State, NGO)
Habitat Associations
Macrohabitat: Habitats
range from small creeks, rivers, lakes, and reservoirs to the open ocean.
Sea-run rainbow trout are called steelhead (Ross 2001).
Mesohabitat: Most can
grow well at 17-20°C, but they cannot
tolerate water temperatures above 28-29°C
(Lee and Rinne 1980), and they seem to prefer water temperatures around 11°C
(McCauley et al. 1977). Populations introduced in North Carolina inhabit the
lower reaches of cool-water streams, shaded pools, runs, and riffles (Larson
and Moore 1985; Lohr and West 1992). Fry emerge from gravel 2-3 weeks after
hatching and live in quiet waters close to shore (Moyle 1976).
Biology
Spawning season: Time
of spawning is variable, with introduced populations in the southeast
reproducing during the cooler months, from November through February or
March (Carlander 1969). During April, in Tennessee, individuals emerge from
redds suggesting that spawning occurs in March (Whitworth and Strange 1983).
In New York, spawning occurs late spring or summer (Johnson and Ringler
1981). In California, wild rainbow trout spawn in the spring from February
to June; low temperatures in high mountain areas may delay spawning until
July or August (Moyle 1976).
Spawning location:
Lithophils, rock and gravel spawners that do not guard their eggs (Simon
1999).Generally spawning occurs in streams, rather than lake habitats, with
fertilized eggs buried in the gravel of the redd (Carlander 1969; Tautz and
Groot 1975; Newcombe and Hartman 1980).
Reproductive strategy:
Nonguarders; brood hiders (Simon 1999). With the male hovering above,
chasing away intruders, the female excavates a redd. After she completed the
nest, the female signals the male to initiate spawning (Tautz and Groot
1975; Newcombe and Hartman 1980). After spawning is complete, the redd is no
longer defended (Carlander 1969).
Fecundity: Rainbow
trout usually spawn once a year; fish may skip a year between spawnings.
Number of eggs laid per female ranges from 200-12,000 eggs, depending on
size and origin of the fish. Fish under 30 cm TL typically contain less than
1,000 eggs. Eggs hatch in 3-4 weeks at water temperature of 10-15 degrees C
(Moyle 1976)
Age at maturation:
Highly variable, and is influenced by growth rates and whether or not the
population is migratory (Ross 2001). Nonandromous rainbow trout mature in
their 2nd or 3rd year, but time of first maturity can
vary from the 1st-5th year of life (Moyle1976).
Migration: Andromous
populations (like Pacific coastal O. mykiss, called steelheads)
occupy coastal streams. Resident nonmigratory populations are found farther
inland (Robison and Buchanan 1988).
Longevity: 11 years
(Carlander 1969). Trout in landlocked streams rarely live longer than 3 or 4
years (Northcote 1981; Whitworth and Strange 1983).
Growth: In Tennessee,
rainbow trout measured 104 mm TL at one year, and 186 mm TL by their second
year (Whitworth and Strange 1983). Moyle (1976) notes variability of growth
rates in rainbow trout: In mountain lakes fish reach 11-17 cm TL in their
first year, 14-21 cm TL in their second 20-23 cm TL in their third; seldom
living longer than 6 years or growing over 40 cm TL. Growth rates are
similar in small California streams. In California, most rapid growth is
achieved in large lakes and reservoirs with trout in one lake population
measuring 20-23 cm TL at one year old, 43-46 cm TL at two years old, and
46-56 cm TL at three years old; similar growth achieved by fish planted in
some reservoirs, but generally somewhat slower, especially after first year.
Food habits:
Invertivore/carnivore feeding on invertebrates, other fish, and fish eggs
(Goldstein and Simon 1999). Diet includes wide variety of foods, depending
upon body size and habitat. Caddisflies, stoneflies, mayflies, and crane
flies are important foods for fish inhabiting small streams, as well as
large items including crayfishes, salamanders, and frogs. Terrestrial prey
consumed include: earthworms, beetles, butterflies, moths, bees, and wasps,
and may constitute almost half of diet (Needham 1969; Johnson 1981; Cada et
al. 1987). Daphnids may also be major food item in lake populations, though
rainbow trout are size selective, feeding only on prey in excess of 1.3 mm
(Galbraith 1967). Species will feed in a stream while maintaining position
in current velocities of 13-21 cm/s. Feeding habitat is based largely on
prey capture success (Hill and Grossman 1993). Dominant hierarchy among
resident fish will determine the division of feeding stations in a stream;
these being defended (Jenkins 1969). Individuals weighing in excess of 1-2
kg usually feed primarily at night and take large prey such as fishes
(Needham 1969). Smaller rainbow trout (less
than 90 mm, 12 g) tend to be inactive at night (Hill and Grossman 1993). A
study of rainbow trout in the Guadalupe River tailwater below Canyon
Reservoir, Texas, found this species to actively pursue drift prey of
baetids, chironomid pupae, and helicopsychid adults. Drift declined during
summer months and foraging efforts appeared to be concentrated on the
benthos, with ephemerids and pleurocerid snails abundant in diet (Halloran
2000).
Phylogeny and morphologically similar fishes
Oncorhynchus mykiss
differ from Salmo trutta, the brown trout, in having dark spots on
caudal fin and sides without orange or red spots in life. O. mykiss
differ from O. clarki, the cutthroat trout, in having fewer than 150
lateral line scales, no teeth on midline of tongue, and no red cutthroat
mark (Robison and Buchanan 1988).
Host Records
Trematoda (4), Cestoda (1),
Nematoda (1), Acanthocephala (3), Crustacea (1) (Hoffman 1967; listed as
Salmo mykiss).
Commercial or Environmental Importance
References
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