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Coastal Rainbow trout were originally present in virtually all perennial coastal streams from San Diego north to the Smith River (Del Norte County), and in most rivers in the Central Valley from the Kern River north to the Pit River near Alturas (Modoc County). Resident Coastal Rainbow trout were typically found upstream of natural barriers, such as waterfalls or rockslides, which were too difficult for steelhead to pass. Today, due to numerous introductions, Coastal Rainbows are found in virtually all streams where suitable habitat exists, including the once-fishless Sierra Nevada north of the upper Kern River Basin and lakes and streams in the Cascade Range and Trinity Alps.
Coastal Rainbow trout are incredibly adaptable to different environments and are capable of exhibiting a wide range of coloration. Trout from small streams may be dark olive on the back with a yellowish belly and orange tips on the fins, while lake-dwelling fish tend to be more silver in color. Most Coastal Rainbow trout have heavy, irregular spotting, and spots that radiate outward in lines on the tail and a white belly. The pink to deep red band on their flanks gives the fish its namesake. In waters with access to the ocean, any rainbow trout greater than 41 cm (16 in.) in length are considered to be “steelhead” for management purposes and catch limits, although resident Coastal Rainbow trout regularly attain this size where habitat is favorable and food is plentiful.
Wild resident Coastal Rainbow trout are more abundant today than they were historically in California due to a long history of introductions by pack mule trains, airplanes, and other means, especially into previously fishless high elevation lakes in the Sierra Nevada. However, Coastal Rainbow trout abundance across California was likely depressed during the historic drought (2012-16) based on drought rescue information from CDFW.
Coastal rainbows mature when they are two or three years old, and rarely live more than five or six years. They generally spawn in spring to early summer, from February to June depending on stream temperatures, but have been known to spawn during the winter months in Putah Creek (Solano County) and may spawn year-round in spring-fed streams such as the Fall River (Shasta County) without strong seasonal cues such as flow or temperature. Fish that spend their entire lives in fresh water rarely attain sizes greater than 70 cm (28 in.), but lake-dwelling fish may grow larger. In rivers and streams, they feed on aquatic and terrestrial insects that drift in the water column, and may occasionally eat fish and frogs, especially as they grow larger. They may feed on small invertebrate worms or insect larvae on the bottom of some rivers and lakes. In lakes and reservoirs, they frequently feed on fish such as Threadfin shad. Coastal Rainbow trout owe their success to their ability to adapt to a wide variety of habitats. They are capable of being stream residents, lake residents, or migratory between these habitats. Coastal Rainbow trout that express one life history are capable of having offspring that take on another life history if habitat is available.
Coastal Rainbow trout are defined in this report as self-sustaining Rainbow trout populations that are (a) isolated above natural barriers as the result of geologic activity (landslides, waterfalls, etc.), (b) isolated above anthropogenic barriers, such as dams, and/or (c) introduced by people into isolated areas, such as historically fishless lakes of the Sierra Nevada. While all Coastal Rainbow trout likely had steelhead ancestors, populations upstream of major dams today have been found to be more genetically similar to other above-dam populations than they are to fish downstream of dams. Despite over a century of widespread stocking of hatchery strains of Coastal Rainbow trout in California, many populations above man-made barriers share relatively little genetic material with hatchery Rainbow trout.
Peter Moyle is the Distinguished Professor Emeritus in the Department of Wildlife, Fish and Conservation Biology and Associate Director of the Center for Watershed Sciences, at UC Davis. He is author or co-author of more than 240 publications, including the definitive Inland Fishes of California (2002). He is co-author of the 2017 book, Floodplains: Processes and Management for Ecosystem Services. His research interests include conservation of aquatic species, habitats, and ecosystems, including salmon; ecology of fishes of the San Francisco Estuary; ecology of California stream fishes; impact of introduced aquatic organisms; and use of floodplains by fish.
Robert Lusardi is the California Trout/UC Davis Wild and Coldwater Fish Researcher focused on establishing the basis for long-term science specific to California Trout’s wild and coldwater fish initiatives. His work bridges the widening gap between academic science and applied conservation policy, ensuring that rapidly developing science informs conservation projects throughout California. Dr. Lusardi resides at the UC Davis Center for Watershed Sciences and works closely with Dr. Peter Moyle on numerous projects to help inform California Trout conservation policy. His recent research interests include Coho salmon on the Shasta River, the ecology of volcanic spring-fed rivers, inland trout conservation and management, and policy implications of trap and haul programs for anadromous fishes in California.
Patrick Samuel is the Conservation Program Coordinator for California Trout, a position he has held for almost two years, where he coordinates special research projects for California Trout, including the State of the Salmonids report. Prior to joining CalTrout, he worked with the Fisheries Leadership & Sustainability Forum, a non-profit that supports the eight federal regional fishery management councils around the country. Patrick got his start in fisheries as an undergraduate intern with NOAA Fisheries Protected Resources Division in Sacramento, and in his first field job as a crew member of the California Department of Fish & Wildlife’s Wild and Heritage Trout Program.
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Dams block access to historical spawning and rearing habitats. Downstream, dams alter the timing, frequency, duration, magnitude, and rate of change of flows decreasing habitat quality and survival.
The findings from this study have made it clear – the time to act is now. We can work together to ensure that California will always have resilient populations of wild fish thriving in clean, cold water streams.
Here are some things you can do today:
This factor refers to hard rock mining, from which contaminated tailings, mine effluents, and toxic pollutants may have been dumped or leached into streams, mostly from abandoned mines. Mercury mining, used for processing gold in placer and dredge mining, left a lasting negative impact on wildlife.
Hatcheries and releases of hatchery reared salmonids into the wild can negatively impact wild populations through competition, predation, disease, and loss of fitness and genetic diversity. Hatchery influences are especially apparent to for anadromous species where dams blocked access to spawning habitat and hatcheries were established as mitigation. Inland trout can also be impacted with stocking of hatchery fish for recreation.
All anadromous salmonids depend on estuaries for rearing during a portion of their lives. Most estuaries in the state are highly altered from human activities, especially diking, draining, and sandbar removal between the estuary and ocean. Land-uses surrounding estuaries often involve extensive wetland reclamation, greatly reducing ecological function and habitat complexity.
Harvest relates to legally regulated commercial, tribal, and recreational fisheries, as well as illegal harvest (poaching). Over-harvest can have substantial impacts on fish populations, particularly for those with already limited abundance or distributions, those which are isolated or reside in discrete habitats making them easy to catch (e.g. summer steelhead), or those that attain large adult size (e.g., Chinook salmon).
Transportation corridors such as highways confine stream channels and increase sedimentation, pollution, and habitat degradation from storm runoff and altered streamflows. Culverts and other passage or drainage modifications associated with roads often block migration and restrict fish movements, which can fragment populations.
Many heavily logged watersheds once supported the highest species diversity and abundance of fishes, including anadromous salmon and steelhead. Improperly managed logging increases sediment in streams, increases solar input which increases stream temperatures, and degrades riparian cover. Stream habitat is also degraded by the extensive network of unpaved roads that supports timber extraction.
Non-native species (including fishes and other aquatic organisms) are ubiquitous across many of California’s watersheds; their impacts on native species through hybridization, predation, competition, increased disease transmission, and habitat alteration can be severe.
Wildfires are a natural component of California’s landscape. However, fire suppression, coupled with climate change, has made modern fires more frequent, severe and catastrophic. The transition from relatively frequent understory fires to less frequent, but catastrophic, crown fires can have a severe impact on fish habitat and wipe out populations with narrow habitat ranges.
Impacts from agriculture include streams polluted by agricultural return water or farm effluent; reduced flow due to diversions which can affect migratory patterns; and increased silt and pesticides in streams. Marijuana grow operations, legal and illegal, were considered in this metric.
As California’s population grows, rural development increasingly encroaches along or near streams. Resulting impacts include water diversions, groundwater pumping, streambed alteration (to protect houses from flooding, construct road crossings, etc.), and pollution (especially from septic tanks and illegal waste dumping).