Research, Monitoring, and Evaluation of Avian Predation on Salmonid Smolts in the Lower and Mid‐Columbia River
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Bonneville Power Administration, USACE – Portland District, USACE – Walla Walla District, and Grant County Public Utility District Research, Monitoring, and Evaluation of Avian Predation on Salmonid Smolts in the Lower and Mid‐Columbia River 2013 Draft Annual Report 1 2013 Draft Annual Report Bird Research Northwest Research, Monitoring, and Evaluation of Avian Predation on Salmonid Smolts in the Lower and Mid‐Columbia River 2013 Draft Annual Report This 2013 Draft Annual Report has been prepared for the Bonneville Power Administration, the U.S. Army Corps of Engineers, and the Grant County Public Utility District for the purpose of assessing project accomplishments. This report is not for citation without permission of the authors. Daniel D. Roby, Principal Investigator U.S. Geological Survey ‐ Oregon Cooperative Fish and Wildlife Research Unit Department of Fisheries and Wildlife Oregon State University Corvallis, Oregon 97331‐3803 Internet: [email protected] Telephone: 541‐737‐1955 Ken Collis, Co‐Principal Investigator Real Time Research, Inc. 52 S.W. Roosevelt Avenue Bend, Oregon 97702 Internet: [email protected] Telephone: 541‐382‐3836 Donald Lyons, Jessica Adkins, Yasuko Suzuki, Peter Loschl, Timothy Lawes, Kirsten Bixler, Adam Peck‐Richardson, Allison Patterson, Stefanie Collar, Alexa Piggott, Helen Davis, Jen Mannas, Anna Laws, John Mulligan, Kelly Young, Pam Kostka, Nate Banet, Ethan Schniedermeyer, Amy Wilson, and Allison Mohoric Department of Fisheries and Wildlife Oregon State University Corvallis, Oregon 97331‐3803 2 2013 Draft Annual Report Bird Research Northwest Allen Evans, Bradley Cramer, Mike Hawbecker, Nathan Hostetter, and Aaron Turecek Real Time Research, Inc. 52 S.W. Roosevelt Ave. Bend, Oregon 97702 Jen Zamon NOAA Fisheries – Pt. Adams Biological Station, 520 Heceta Street, Hammond, OR 97121 David Kuligowski NOAA Fisheries, 7305 Beach Drive East, Port Orchard, WA 98366 Submitted: February 28, 2014 3 2013 Draft Annual Report Bird Research Northwest TABLE OF CONTENTS EXECUTIVE SUMMARY………………………………....…………………………………………………………. 7 INTRODUCTION…………………………………..…………………………………………………………………… 13 STUDY AREA………………………………….…...…………………………………………………………………... 16 SECTION 1: CASPIAN TERNS……………………………………………………………………………………... 16 1.1. Preparation and Modification of Nesting Habitat……………………………………………... 16 1.1.1. Columbia River Estuary……………………….…………………………………………………. 17 1.1.2. Interior Oregon and Northeastern California…………….…………………………… 18 1.2. Colony Size and Productivity……………………………………………….…………………………….. 19 1.2.1. Columbia River Estuary……………………….…………………………………………………. 19 1.2.2. Columbia Plateau………………………..………………………………………………………... 21 1.2.3. Coastal Washington……………………….……………………………………………………... 24 1.2.4. Interior Oregon and Northeastern California…………….…………………………… 29 1.3. Diet Composition and Salmonid Smolt Consumption………………………………………… 32 1.3.1. Columbia River Estuary……………………….…………………………………………………. 32 1.3.2. Columbia Plateau………………………..………………………………………………………... 34 1.3.3. Coastal Washington……………………….……………………………………………………... 36 1.3.4. Interior Oregon and Northeastern California…………….…………………………… 36 1.4. Predation Rates Based on Smolt PIT Tag Recoveries……………….…………………………. 38 1.4.1. Columbia River Estuary……………………….…………………………………………………. 42 1.4.2. Columbia Plateau………………………..………………………………………………………... 44 1.4.3. Coastal Washington……………………….……………………………………………………... 50 1.4.4. Interior Oregon and Northeastern California…………….…………………………… 50 1.5. Color Banding and Band Re‐sightings…………………....…...……………………………………. 51 1.5.1. Columbia River Estuary……………………….…………………………………………………. 52 1.5.2. Columbia Plateau………………………..………………………………………………………... 53 1.5.3. Interior Oregon and Northeastern California…………….…………………………… 54 SECTION 2: DOUBLE‐CRESTED CORMORANTS………………………………………………………….. 57 2.1. Nesting Distribution and Colony Size…………………….…………………………………………… 57 2.1.1. Columbia River Estuary……………………….…………………………………………………. 57 2.1.2. Columbia Plateau………………………..………………...……………………………………… 59 2.1.3. Coastal Washington……………………….……………...……………………………………… 60 2.1.4. Interior Oregon and Northeastern California…………….…………………………… 61 4 2013 Draft Annual Report Bird Research Northwest 2.2. Nesting Success…………………………….……………………..……………………………………………. 61 2.2.1. Columbia River Estuary……………………….…………………………………………………. 61 2.2.2. Columbia Plateau…………………..……………………………………………………………... 62 2.2.3. Coastal Washington……………………….……………...……………………………………… 62 2.2.4. Interior Oregon and Northeastern California…………….…………………………… 62 2.3. Diet Composition and Salmonid Smolt Consumption……………………………………….. 63 2.3.1. Columbia River Estuary……………………….…………………………………………………. 63 2.3.2. Columbia Plateau………………………..………………………………………………………... 65 2.3.3. Coastal Washington……………………….……………...……………………………………… 65 2.3.4. Interior Oregon and Northeastern California…………….…………………………… 66 2.4. Predation Rates Based on Smolt PIT Tag Recoveries…….…………………………………... 66 2.4.1. Columbia River Estuary……………………….…………………………………………………. 66 2.4.2. Columbia Plateau………………………..………………………………………………………... 67 2.5. Color‐banding………………………………………..……………………………....………………………… 68 2.6. Management Feasibility Study………………………..………………………………………………… 69 SECTION 3: OTHER PISCIVOROUS COLONIAL WATERBIRDS……………………………………… 74 3.1. Distribution……………………………….………………………………………………………………………. 74 3.1.1. Columbia River Estuary……………………….…………………………………………………. 74 3.1.2. Columbia Plateau………………………..….…………………………………………………….. 75 3.1.3. Coastal Washington……………………….……………………………………………………... 77 3.1.4. Interior Oregon and Northeastern California…………….…………………………… 77 3.2. Diet Composition…………………………….………………………………………………………………… 78 3.2.1. Columbia River Estuary……………………….…………………………………………………. 78 3.2.2. Columbia Plateau………………………..….…………………………………………………….. 79 3.2.3. Coastal Washington……………………….……………………………………………………... 81 3.2.4. Interior Oregon and Northeastern California…………….…………………………… 81 3.3. Predation Rates Based on Smolt PIT Tag Recoveries……………….………………………… 81 3.3.1. Columbia River Estuary……………………….…………………………………………………. 81 3.3.2. Columbia Plateau………………………..….…………………………………………………….. 82 ACKNOWLEDGMENTS………………………………………………………………………………………………. 86 LITERATURE CITED…………………………………...……………………………………………………………… 88 PROJECT PUBLICATIONS AND SUBMITTED MANUSCRIPTS………………………….……………. 98 5 2013 Draft Annual Report Bird Research Northwest PROGRAM FUNDING………………………………...…………………………………………………………….. 102 MAPS…………………………………….….……………………………………………………………………………… 105 FIGURES…………………………………….…………………………………………………………………………….. 111 TABLES……………………………………..……………………………………………………………………………… 184 APPENDIX A: PIT TAG DEPOSITION STUDIES…………………………………………………………….. 193 APPENDIX B: PREVIOUSLY REPORTED CASPIAN TERN PREDATION RATES ADJUSTED FOR SMOLT PIT TAG DEPOSITION RATE, 2007‐2013..……….…………………… 208 APPENDIX C: FORAGING BEHAVIOR AND DISPERSAL PATTERNS OF CASPIAN TERNS NESTING ON GOOSE ISLAND, POTHOLES RESERVOIR…………………….. 210 6 2013 Draft Annual Report Bird Research Northwest EXECUTIVE SUMMARY The primary objectives of this project in 2013 were to (1) evaluate the efficacy of management initiatives implemented to reduce predation on juvenile salmonids (Oncorhynchus spp.) by Caspian terns (Hydroprogne caspia) nesting on East Sand Island in the Columbia River estuary, including the monitoring of alternative Caspian tern nesting islands built by the Corps outside the Columbia River basin; (2) collect, compile, and analyze data needed to assist in completion of the NEPA analysis required for management of (a) double‐crested cormorants (Phalacrocorax auritus) nesting on East Sand Island and (b) Caspian terns nesting at colonies in the Columbia Plateau region; (3) investigate the numbers of other piscivorous colonial waterbirds (i.e., Brandt’s cormorants P. penicillatus, California brown pelicans Pelecanus occidentalis californicus, American white pelicans P. erythrorhynchos, and gulls Larus spp.) that use the Columbia River to nest or roost and assess their potential impacts on smolt survival; and (4) assist resource managers as technical advisors in the development of plans for long‐term management of avian predation on juvenile salmonids from the Columbia River basin, as warranted. The Caspian tern colony on East Sand Island, the largest for the species in the world, consisted of about 7,400 breeding pairs in 2013. This is an increase from the estimate of 6,400 pairs in 2012, and the first increase since the initiation of habitat reduction on East Sand Island in 2008, when the colony numbered about 10,000 breeding pairs. In addition to the increase in colony size, Caspian terns at this colony were more resilient to disturbances by bald eagles and associated gull depredation on tern eggs and chicks compared to during 2010‐2012. The Caspian tern colony on East Sand Island produced about 1,480 fledglings in 2013 (average of 0.20 young raised/breeding pair), a significant increase from 2010‐2012 (average of 0 ‐ 0.06 young raised/breeding pair), but lower than in other years during 2001‐2009. The average proportion of juvenile salmonids in the diet of Caspian terns during the 2013 nesting season was 32%, similar to 2009‐2012. The estimated total smolt consumption by Caspian terns nesting at East Sand Island in 2013 was 4.6 million (95% c.i. = 3.9 ‐ 5.3 million), similar to 2012. Recoveries of smolt passive integrated transponder (PIT) tags on the Caspian tern colony at East Sand Island indicated that tern predation rates on salmonid smolts that were interrogated passing Bonneville Dam on the Columbia River or Sullivan Dam on the Willamette River were similar in 2013 and 2012. Also similar to previous