E.D. Chapman, A.R. Hearn, A.P. Klimley, P.E. LaCivita, W.N. Brostoff & A.M. Bremner

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Migration of late-fall Chinook and steelhead smolts relative to dredge removal and disposal sites in San Francisco Bay US Army Corps of Engineers E.D. Chapman, A.R. Hearn, A.P. Klimley, P.E. LaCivita, W.N. Brostoff & A.M. Bremner

The California Fish Tracking Consortium 10 organizations 100s of monitors 1000s of fish tagged

Range of studies Spawning behavior, migrations, survival, juvenile movements, anthropogenic effects, restoration and climate change, niche partitioning. And plenty more!

The array: Backbone of it all

Study Questions 1. What are the general migratory patterns of salmonid smolts through SF Bay in relation to dredge and dredge placement sites? 2. What is the residence time of these fish A) in particular reaches of the estuary (transit time) and B) at sites of interest (exposure time)? 3. What are the spatial and temporal distribution patterns of green sturgeon in the estuary?

Study Species Late-fall Chinook Salmon Steelhead Year Fish tagged 2006/7 49 2007/8 50 2008/9 500 2010 500 Year Fish tagged 2006/7 49 2007/8 50 2008/9 500 2010 500

New Species: Green Sturgeon Over 300 green sturgeon tagged in the last 5 years. Tagging ongoing (six last week!) Several projects look at effects of Red Bluff Dam, migration upriver, juvenile habitat use etc. Current perception that adult green sturgeon are in the estuary all year round and over the entire area.

Fish Tagging

Study Array

Range Tests 70% at 75 m radius

Q1: What are the general migratory patterns of salmonid smolts through SF Bay in relation to dredge and dredge placement sites?

01/03/2009 03/03/2009 05/03/2009 07/03/2009 09/03/2009 11/03/2009 13/03/2009 15/03/2009 17/03/2009 19/03/2009 21/03/2009 23/03/2009 25/03/2009 27/03/2009 29/03/2009 31/03/2009 02/04/2009 04/04/2009 06/04/2009 08/04/2009 10/04/2009 12/04/2009 14/04/2009 16/04/2009 18/04/2009 20/04/2009 22/04/2009 24/04/2009 26/04/2009 28/04/2009 30/04/2009 01/03/2009 03/03/2009 05/03/2009 07/03/2009 09/03/2009 11/03/2009 13/03/2009 15/03/2009 17/03/2009 19/03/2009 21/03/2009 23/03/2009 25/03/2009 27/03/2009 29/03/2009 31/03/2009 02/04/2009 04/04/2009 06/04/2009 08/04/2009 10/04/2009 12/04/2009 14/04/2009 16/04/2009 18/04/2009 20/04/2009 22/04/2009 24/04/2009 26/04/2009 28/04/2009 30/04/2009 Dispersal and Survival 140 120 Benicia A Carquinez A Richmond A Golden Gate A Benicia B Carquinez B 140 120 Benicia A Carquinez A Richmond A Golden Gate A Benicia B Carquinez B Richmond B Golden Gate B Richmond B 100 Golden Gate B 100 80 80 60 60 40 40 20 20 0 0 Steelhead Late Fall Chinook

Sloshing Many fish (both species) display repeated upstream-downstream movements, coinciding with tidal flows

Direct Routes? Instantaneous rates of transit through experimental array were faster than overall transit through reach (Paired t-test, p<0.001) Why? (flats, backforth washing, pausing?) Chinook salmon

Q2a: What is the residence time of salmonid smolts in particular reaches of the estuary (transit time)?

Results to Date N: 118 65 58 43 48 31 Transit time from Benicia to the Golden Gate Transit time of Chinook salmon (LFC, grey) and steelhead (STH, white) in three sections of the Sacramento River system: Benicia (BEN) Carquinez (CAR), Carquinez (CAR) Richmond (RIC), Richmond (RIC) Golden Gate (GG).

Results to Date Transit rates (ms-1) for Chinook salmon (filled bars) and steelhead (white bars) from Benicia Bridge to Carquinez Bridge, 2009. Transit rates (ms-1) for Chinook salmon (filled bars) and steelhead (white bars) from Carquinez Bridge to Richmond Bridge, 2009. Transit rates (ms-1) for Chinook salmon (filled bars) and steelhead (white bars) from Richmond Bridge to the Golden

Q2b: What is the residence time of salmonid smolts at sites of interest (exposure time)?

General Exposure Time Total exposure time at a dredged site (marina or channel) by salmonid smolts in San Francisco Bay Estuary.

Fish Presence at Dredged Sites Chinook salmon Station Type Station Name # Fish # Detection Marina/ Shoal Berkley Marina # Fish Steelhead # Detection EmeryvilleA EmeryvilleB 1 2 G3 5 160 2 22 G5 1 1 Larkspur Ferry 15 5 112 MartinezMarina 156 1152 64 162 MontezumaEast 4 308 4 149 MontezumaWest 4 103 2 22 PetalumaRRBridge 5 192 5 206 Point Richmond 2 30 PortSonomaMarina 4 50 3 7 San Rafael Can 6 Suisun City Marina Vallejo Marina C 12 36 Total 168 2003 77 711 Channel SPBuoy7 1 1 SPBuoy8 50 331 38 163 SPBuoy10 38 240 2 5 SPBuoy10b 3 7 Total 80 578 39 169

Summary Bay movements of salmonids affected by tidal influences, leading to a washing effect up and down stream Instantaneous transit rates > overall transit rates; movements may not be entirely directional within channels, but may include use of flats Overall transit times through the Bay is relatively short; less than 10 days Reach specific transit rates variable for both species and range from 0.1-1.9 ms -1 Cumulative exposure at dredge site monitors was low for both species; less than 12 minutes for most individuals

Q3: What are the spatial and temporal distribution patterns of green sturgeon in the estuary?

Distribution of Green Sturgeon in the Bay Program IEP Monitoring Program Sampling Method Sampling gear # Fish Size Range (cm) Various 23 19-101 CDFG Trammel Trammel Net 732 47-209 UC Davis Gill Net 209 55-204 N=746

Seasonal Presence of Tagged Sturgeon (135 cm) (160 cm) (200 cm) Examples from individuals

Number of fish Transit Rates Through Bay Studied overall transit rates from Rio Vista to Carquinez and from Carquinez to Golden Gate Fish moved faster in winter than fall (P = 0.009) Fish moved faster downstream than upstream (P=0.032) No difference in transit rates by reach (upper and lower) 7 6 5 Median up down 4 3 2 1 0 0 4 8 12 16 20 24 28 32 36 40 44 48 Transit rate (km/day)

Movements Around Placement Site SF10

Exposure at dredged sites From March-June 2009, 18 fish detected in Bay, 10 detected at dredged sites (exposure time [min]) Tag ID Martinez Marina Richmond Point Vallejo Marina G3 Channel Total 217 34.3 20.2 54.6 219 682.5 682.5 224 18.6 18.6 2204 21.1 9.6 30.8 2237 7.1 7.1 2242 11.6 11.6 5447 252.7 149.8 402.5 5449 57.1 57.1 5450 30.7 30.7 10816 173.4 173.4 Average Minutes 74.4 15.9 416.1 9.6 146.9 (Two individuals (Tag IDs # 217 and 2237) were detected at the Alcatraz SE monitor for 21 minutes (13+8) and a single detection, respectively).

Expected Results 2010 Describe frequency use of shallow flats/shoals for all three species Channel preference through SP Bay and Raccoon Strait. Transit time in relation to tidal state and currents (ADCP work) How much time do sturgeon spend in the estuary? Inter-annual variations (dry years vs. wet years?) Diel influence on behavior and movement patterns

Future Steps Towards an ecosystem-based management: suite of native species (including green sturgeon, sevengill sharks). Climatic influence on migratory behavior (wet vs dry years) Fine scale movements and avoidance behavior in relation to human activities. Transit time in relation to tidal state and currents (ADCP work) Integration of South Bay sites?

Acknowledgements We would like to thank Mike McGill and Christina Slager at the Aquarium of the Bay for providing the boat time to deploy and maintain the monitors deployed on acoustical releases. Thanks to Dave Vogel for allowing us to present data on three green sturgeon tagged by his project. We would also like to thank Chuck Morton for scheduling boat time and assisting on the Caltrans vessel with the maintenance of the monitors deployed on the Bay Bridge and Richmond San Rafael Bridge. We greatly appreciate the help from everyone in the UC Davis Biotelemetry Laboratory (Denise Tu, Anna Stephenson, Taylor Chapple, Phil Sandstrom, Dennis Cocherell) for volunteering their time to assist with the surgical implantation of the tags. We would also like to thank Arnold Ammann and Cyril Michele at the Santa Cruz office of the NMFS for maintaining the database which made it possible to assemble detections from many different studies. We would like to acknowledge David Woodbury at the Santa Rosa office of the NMFS for his input into the design of the study. Finally, we would like to thank Pete Lacivita, Bill Brostoff, and Allison Bremner for their efforts in all aspects of the study.