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Programs & DataConservation and ManagementCentral Valley MonitoringStanislaus River Escapement
Stanislaus River Escapement Survey

  • Project Overview
  • Project Location
  • Methods
  • Reports
  • Contacts
The California Department of Fish and Wildlife has been conducting annual escapement surveys on the Stanislaus River to estimate and monitor the number of adult fall-run Chinook salmon (Oncorhynchus tshawytscha) returning to spawn since 1952. Monitoring is conducted within the spawning reach, beginning upstream at Goodwin Dam (River Mile 58) and continuing downstream to Jacob Myers Park in Riverbank (River Mile 33). The current objectives of the escapement monitoring are to:

  1. Using the Cormack-Jolly-Seber method to estimate the escapement of fall run Chinook salmon on the Stanislaus River.
  2. Evaluate the distribution of salmon redds throughout the study area.
  3. Collect fork-length and sex data.
  4. Collect scale and otolith samples to conduct age determination and subsequent cohort analysis.
  5. Collect and analyze coded wire tag data from marked adipose fin clipped fish to determine escapement contribution of hatchery produced salmon.
  6. Escapement estimate and spawning data collected are used in evaluating the recovery of the species and fishery restoration in the basin.

The tranquil moment before a busy carcass survey day on the Stanislaus River.
CDFW staff extracting biological samples from a salmon carcass.
A processed salmon carcass.
A male Chinook salmon carcass.
CDFW staff extracting biological samples from a salmon carcass.
Project Location

Stanislaus River Escapement Map
Stanislaus River Escapement Map

Stanislaus River - Escapement Monitoring Methods


Fall run Chinook salmon surveys are typically conducted on the Stanislaus River for three to four days per week from October through early January, with some annual variation depending on the number of returning salmon and environmental conditions. Surveys are conducted using a drift boat, kayaks, or on foot. Crew members will count all live fish and redds observed for each riffle while moving downstream.

Traditional mark-recapture methods were used to estimate fall run escapement on the Stanislaus River. Using these methods, carcasses are marked and subsequently recovered during weekly surveys of the spawning reach. A ratio of total fish handled to number of recoveries is used to calculate the total spawning population.

All visible carcasses are collected from each riffle and the pool immediately below. Each carcass handled is designated as fresh, decayed, skeleton, or recovery depending on the degree of decomposition or the presence of an aluminum jaw tag in the case of recoveries. Recoveries are recorded on the data sheet and returned to the river. Skeletons are in an advanced state of decay or have signs of predation and are enumerated and then chopped in half to avoid double counting in future surveys. Fresh and decayed carcasses are sampled to record sex, fork length, and adipose fin presence. A round disc tag is attached to the lower jaw as part of the mark-recapture study. Scales and otoliths are collected for age analysis. If no adipose fin is observed, the upper portion of the head is removed for later coded wire tag (CWT) extraction. CWT’s are analyzed to determine the hatchery of origin, release date and location, and fish age.

Reports

2022 Stanislaus River Fall Chinook Salmon Escapement Survey

Contact Information

Ryan Kok, Environmental Scientist
California Department of Fish and Wildlife
La Grange Field Office
PO Box 10 La Grange, CA 95329
Ryan.Kok@wildlife.ca.gov


Steve Tsao, Sr. Environmental Scientist
California Department of Fish and Wildlife
La Grange Field Office
PO Box 10 La Grange, CA 95329
steve.tsao@wildlife.ca.gov


2018 by CalFish
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