Populations of many rainbow trout subspecies, including anadromous forms (steelhead) of (coastal rainbow trout) and (Columbia River redband trout), have declined in their native ranges due to over-harvest, habitat loss, disease,
invasive species, pollution and hybridization with other subspecies, and some introduced populations, once healthy, have declined for the same reasons. As a consequence, some rainbow populations, particularly anadromous forms within their native range, have been classified as
endangered,
threatened or species of special concern by federal or state agencies. Rainbow trout, and subspecies thereof, are currently a
U.S. Environmental Protection Agency-approved indicator species for acute freshwater
toxicity testing. Many non-profit organizations have formed to protect, conserve and restore native rainbow trout and steelhead populations. Generally, in partnership with various universities, state, federal and tribal agencies, and private interests, these organizations sponsor projects to restore habitat, prevent habitat loss and promote awareness of threats to native trout populations.
Trout Unlimited (TU) is a non-profit organization dedicated to the conservation of North American freshwater streams, rivers, and associated upland habitats for trout, salmon, other aquatic species, and people. A typical TU project is the Circle Creek Fish Passage Project, in which access to a spawning stream is being improved for steelhead and other salmonid species. The
Wild Salmon Center, an international coalition of Russian, Canadian and U.S. scientists, sponsors the Kamchatka Steelhead Project, a 20-year (1994–2014) scientific program to study and conserve the present condition of Kamchatkan steelhead ("mikizha"), a species listed in the
Red Data Book of Russia. Other high-profile organizations involved in rainbow trout conservation include
California Trout, which protects wild trout and other salmonids in the waters of California. The Steelhead Society of British Columbia promotes the wellbeing of wild salmonids in British Columbia. In 1997, a group of approximately 40 ichthyologists, biologists and naturalists from several U.S. and Mexican institutions formed a collaborative group—Truchas Mexicanas—to study the diversity of
Mexican native trout, most of which are considered subspecies of .
Hybridization and habitat loss Rainbow trout, primarily hatchery-raised fish of the coastal rainbow trout subspecies introduced into waters inhabited with cutthroat trout, will breed with cutthroats and produce fertile hybrids called
cutbows. In the case of the
westslope cutthroat trout (
O. clarki lewisi), hybridization with introduced rainbow and
Yellowstone cutthroat trout (
O. clarki bouvieri) is threatening the westslope cutthroat trout with
genomic extinction. Such introductions into the ranges of redband trout ,
newberrii, and
stonei) have severely reduced the range of pure stocks of these subspecies, making them "species of concern" in their respective ranges. Within the range of the Kern River golden trout of Southern California, hatchery-bred rainbows introduced into the Kern River have diluted the genetic purity of the
Kern River rainbow trout and
golden trout through intraspecific breeding. The
Beardslee trout , a genetically unique lake-dwelling variety of the coastal rainbow trout that is isolated in
Lake Crescent (Washington), is threatened by the loss of its only spawning grounds in the
Lyre River to
siltation and other types of habitat degradation.
Invasive species and disease Whirling disease is a
myxosporean
parasite of
salmonids (salmon, trout, and their allies) that causes whirling disease in pen
farmed salmon and trout and also in
wild fish populations. It was first described in rainbow trout introduced to Germany a century ago, but its range has spread and it has appeared in most of Europe, northern Asia, the U.S., South Africa and other countries. In the 1980s, was found to require
Tubifex tubifex (a kind of
segmented worm) to complete its
life cycle. The parasite infects its hosts with its cells after piercing them with
polar filaments ejected from
nematocyst-like capsules. The parasite was first recorded in North America in 1956 in Pennsylvania, but until the 1990s, whirling disease was considered a manageable problem affecting only rainbow trout in hatcheries. It eventually became established in the natural waters of the Rocky Mountain states (
Colorado, Wyoming,
Utah,
Montana,
Idaho,
New Mexico), where it is damaging several sport fishing rivers. Some streams in the western U.S. lost 90 percent of their trout. Whirling disease threatens recreational fishing, which is important for the tourism industry, a key component of the economies of some U.S. western states. For example, in 2005 anglers in Montana spent approximately $196,000,000 in activities directly related to trout fishing in the state. Some of the salmonids that infects (
bull trout,
cutthroat trout, and anadromous forms of rainbow trout—steelhead) are already threatened or endangered, and the parasite could worsen their population decline.
New Zealand mud snail The
New Zealand mud snail , once
endemic to New Zealand, has spread widely and has become
naturalised and an invasive species in many areas including Australia, Asia (Japan,), Europe (since 1859 in England), and North America (U.S. and Canada:
Thunder Bay in Ontario since 2001, British Columbia since July 2007), most likely inadvertently during human activity. There is evidence North American fishes are unable to digest the tiny but hard shells of the mud snail, and that their presence may result in poor growth outcomes for rainbow trout. The mud snail was first detected in the U.S. in Idaho's Snake River in 1987. Since then, the snail has spread to the
Madison River, Firehole River, and other watercourses around Yellowstone National Park, and has been discovered throughout the western U.S. The exact means of transmission is unknown, but it is likely that it was introduced in water transferred with live
game fish and has been spread by
ship ballast or contaminated recreational equipment such as
wading gear.
Didymo , commonly known as didymo or rock snot, is a species of
diatom that produces nuisance growths in freshwater rivers and streams with consistently cold water temperatures. In New Zealand, invasive didymo can form large mats on the bottom of rivers and streams in late winter. It is not considered a significant human health risk, but it can affect stream habitats and sources of food for fish, including rainbow trout, and make recreational activities unpleasant. Even though it is native in North America, it is considered a nuisance organism or invasive species.
Redmouth disease Enteric redmouth disease is a
bacterial infection of freshwater and marine fish caused by the pathogen . It is primarily found in rainbow trout and other cultured
salmonids. The disease is characterized by
subcutaneous hemorrhaging of the mouth, fins, and eyes. It is most commonly seen in fish farms with poor water quality. Redmouth disease was first discovered in Idaho rainbow trout in the 1950s.
Removal methods Some fisheries are focused on removing rainbow trout in order to reestablish native trout populations. This can be done by poisoning rivers with chemicals such as
antimycin or
rotenone which have been declared safe in the U.S. by the
Environmental Protection Agency. Once the chemicals have dissipated, native trout are released into the river. Another method is to use
electrofishing which enables the fish to be caught alive and harvested or re-located. This technique has been used in the Great Smoky Mountains National Park to rid it of rainbow trout that were introduced in the 1930s and have thrived ever since. They are hoping to re-establish native brook trout in at least some of the river system. Neither method of control is 100% effective and are best regarded as methods to change the relative population sizes of fish species.
Steelhead declines in British Columbia Steelhead populations in parts of its native range have declined due to a variety of human and natural causes. While populations in Alaska and along the British Columbia coast are considered healthy, populations in Kamchatka and some populations along the U.S. West Coast are in decline. The U.S.
National Marine Fisheries Service has 15 identified
distinct population segments, in
Washington,
Oregon, and California. Eleven of these populations are listed under the U.S.
Endangered Species Act, ten as threatened and one as endangered. One distinct population segment on the Oregon coast is designated a U.S.
Species of Concern. The
Southern California distinct population segment, which was listed as endangered in 2011, has been affected by habitat loss due to dams, confinement of streams in concrete channels,
water pollution, groundwater pumping,
urban heat island effects, and other byproducts of urbanization. Steelhead in the Kamchatka Peninsula are threatened by over-harvest, particularly from
poaching and potential development, and are listed in the
Red Data Book of Russia that documents rare and endangered species.
Hatchery stocking influence Several studies have shown that almost all California coastal steelhead are of native origin, despite over a century of hatchery stocking. Genetic analysis shows that the South Central California Coast and Southern California populations from
Malibu Creek north, including the
San Gabriel River,
Santa Ana River, and
San Mateo Creek, are not hatchery strains. Steelhead from
Topanga Creek and the
Sweetwater River were partly, and those from
San Juan Creek completely, of hatchery origin. Genetic analysis has also shown that the steelhead in the streams of the
Santa Clara County and
Monterey Bay basins are not of hatchery origin, including the
Coyote Creek,
Guadalupe River,
Pajaro River,
Permanente Creek,
Stevens Creek,
San Francisquito Creek,
San Lorenzo River, and
San Tomas Aquino Creek basins. Natural waterfalls and two major dams have isolated
Russian River steelhead from freshwater rainbow trout forms above the impassable barriers; a 2007 genetic study of fin samples collected from steelhead at 20 different sites both above and below passage barriers in the watershed found that although 30 million hatchery trout were stocked in the river from 1911 to 1925, the steelhead remain of native and not hatchery origin. Releases of conventionally reared hatchery steelhead pose ecological risks to wild steelhead populations. Hatchery steelhead are typically larger than the wild forms and can displace wild-form juveniles from optimal habitats. The dominance of hatchery steelhead for optimal microhabitats within streams may reduce wild steelhead survival as a result of reduced foraging opportunities and increased rates of predation. ==Uses==