Central California Coast steelhead range from the Russian River (Sonoma County) south to Aptos Creek (Santa Cruz County). Within the San Francisco Bay Estuary, CCC steelhead are found in the Guadalupe and Napa rivers, and San Leandro, San Lorenzo, Coyote, San Francisquito, San Mateo, and Alameda creeks. Populations of CCC steelhead still reside in the upper reaches of streams that feed reservoirs, such as Upper San Leandro Reservoir upstream of Chabot Dam. Some small coastal streams south of the Golden Gate Bridge also contain CCC steelhead, such as Pilarcitos and Pescadero creeks in San Mateo County and Scott and Waddell creeks in Santa Cruz County.
Central California Coast steelhead are anadromous coastal Rainbow trout that live downstream of manmade barriers throughout their range. They are very similar to Northern California winter steelhead in appearance.
Historical abundance estimates of Central California Coast steelhead are limited. During the early 1960s, the California Department of Fish and Wildlife estimated about 94,000 CCC steelhead spawned throughout their range, with most spawning occurring in the Russian (50,000) and San Lorenzo rivers (19,000). With the exception of hatchery-raised steelhead from the Warm Springs Hatchery on the Russian River, most watersheds support less than a few hundred adult steelhead per year. Current populations are likely less than 10% of these historical estimates. For example, CDFW has not documented spawning steelhead in San Francisco Bay tributaries since the drought started in 2012.
All CCC steelhead are winter-run fish, entering freshwater as mature adults during the highest flows of the year, typically between late December and February. Adults returning to freshwater are mostly three and four years old, and typically spawn during late spring (February to April). With favorable flow and temperature conditions, female steelhead may spawn and return to saltwater in only a few weeks, while male fish may linger and spawn multiple times before returning to the ocean. Eggs hatch after about a month in the gravel, with fry emerging and beginning to feed about three weeks later. When juvenile steelhead reach about 10 cm (about 4 in.) in length, they begin to smolt and migrate downstream during spring and summer months to seek out foraging opportunities in larger mainstem rivers or critical estuaries and lagoons. Smolts spend up to two years or more in larger rivers and estuaries putting on weight and roughly doubling in length before their arduous journey to the Pacific Ocean. Once at sea, CCC steelhead migrate to cool waters offshore of the Klamath-Trinidad coastline before moving to feeding grounds in the North Pacific with steelhead from other regions.
CCC steelhead are more closely related to more southerly steelhead populations south of Monterey Bay than they are to populations north of the Russian River. Steelhead from the Russian River (Sonoma County) south to the Golden Gate Bridge form a distinct genetic group, while steelhead from the Golden Gate Bridge south to Big Sur form another.
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).