Evaluation of prototype fish passage structures in the Lower Granite Dam juvenile fish bypass system – juvenile Pacific lamprey results 2013- 2014. Rod.

Slides:



Advertisements
Similar presentations
Action Effectiveness Monitoring in the Upper Columbia (Chapter 4) Karl M. Polivka, Pacific Northwest Research Station, USDA Forest Service.
Advertisements

Smolt Monitoring Program 1982-Present BPA project#
Survival Estimates for the Passage of Juvenile Salmonids Through Dams and Reservoirs of the Lower Snake and Columbia Rivers (Project ) CBFWA March.
Evaluation of Juvenile Salmonid Outmigration and Survival in the Lower Umatilla River Project No Tara White, Shannon Jewett, Josh Hanson,
ISO Adult PIT Interrogation System Installations BPA Project Number July
Eric Hockersmith,Gordon Axel, and Earl Prentice (NOAA Fisheries Service) Development of an Ogee-based PIT-tag Detection System for Spillbays Roger Anderson,
Rebecca A. Buchanan Columbia Basin Research School of Aquatic and Fishery Sciences University of Washington Seattle, WA INVESTIGATING MIGRATORY PROCESSES.
Examining the Effects of Juvenile Migration Timing on Adult Age of Columbia River Salmon Benjamin P. Sandford Fish Ecology Division Fish Ecology Division.
1 Bonneville 2 nd Powerhouse Corner Collector PIT Tag Detection System Project Bonneville Power Administration and U.S. Army Corps of Engineers – Portland.
Methods to Mitigate Tagging Effects (Actual & Perceived) Scott McCutcheon Ryan Richmond Methods to Mitigate Tagging Effects.
History and Development of Pre- loaded Single Use Injectors (SUI) Heiden Bliss Ryan Richmond Scott McCutcheon History and Development of Pre-loaded Single.
A Review of the 2014 Mark Procedures Manual Tiffani Marsh 1, Charles Morrill 2, Pat Keniry 3, Stephen Pastor 4, Jeff Fryer 5, Scott Putnam 6, Brandon Chockley.
Evaluation of a Prototype Spillway Transceiver Gordon Axel, Dr. Sandy Downing, Bruce Jonasson, and Gabriel Brooks Northwest Fisheries Science Center Fish.
Comparing Preloaded PIT Tag Single Use Injectors to Multiple Use PIT Injectors Scott McCutcheon Ryan Richmond Heiden Bliss Comparing Preloaded Single Use.
C. A. Peery, M. L. Keefer, and S. R. Lee Idaho Cooperative Fish and Wildlife Research Unit U.S. Geological Survey and Northwest Fisheries Science Center.
Assessing the use of PIT Tags as a Tool to Monitor Adult Chinook Salmon Returns to Idaho John Cassinelli Regional Fisheries Biologist Idaho Department.
Investigation of Avian Predation Upon Salmonid Smolts With the Use of an Active Acoustic / PIT Tag Combination Curt Dotson – Grant PUD Suzie Rizor – Blue.
Emerging PIT-tag Technologies Presenter: Sandra Downing Ideas and information supplied by numerous people For NPCC Fish Tagging Forum – March 22, 2012.
Update on the status of Snake River Subyearling Chinook Migration Current Year Passage of PIT-tagged Snake Subs LGR PIT Detections LGR Estimated Passage.
Tagging  Fish are captured via angling & implanted with a VEMCO acoustic transmitter (V13, V9, or V7) – (Figure 4).  Specific age classes are targeted.
Survival Estimation Using Estimated Daily Detection Probabilities Benjamin P. Sandford Fish Ecology Division NOAA Fisheries.
Evaluation of the PIT-Tag Detection Arrays in the Priest Rapids Dam Adult Ladders Steve Anglea, Anthony Carson – Biomark, Inc. Eric Lauver – Grant County.
Christopher Caudill, Charles Boggs, Eric Johnson, and Matthew Keefer
Combining PIT Tags with Scale Reading to Better Understand the Life History of Snake River Fall Chinook Salmon Douglas Marsh and William Muir - NOAA Fisheries.
Development of Weir-Wall Contour-Matching PIT Tag Antennas for John Day Dam Adult Ladders PTAGIS Field Office Kennewick, Washington April 2015.
Survival of Migrating Salmonid Smolts in the Snake and Lower Columbia Rivers, 2009 Technical Management TeamDecember 11, 2009 Lessons Learned 2009 Bill.
Documenting O. mykiss life histories in the White Salmon River prior to the reintroduction of anadromous fish above Condit Dam. Brady Allen and Patrick.
Design and Performance of the River Mill Surface Collector
ISAB Snake River 2010 Spill-Transport Review ISAB – Presentation to Council April 14, 2010.
May 10, 2012 Presented by Micki Varney Oregon Department of Fish and Wildlife.
Smolt Monitoring Program: Overview and Data Collection (SMP Traps) Brandon R. Chockley SMP Pre-Season Meeting Feb. 11,
BUILDING STRONG ® PORTLAND DISTRICT 1. BUILDING STRONG ® PORTLAND DISTRICT 2 BiOp Performance Standards for Dam Passage Survival RPA RM&E Actions - Strategy.
COMPARATIVE SURVIVAL STUDY Chapter 3: Annual SAR by study category and ratios of SARs Comparisons of SARs Transport to In-River By hatchery group Hatchery.
Juvenile survival, travel time and the in-river environment Presenter: Steve Haeseker CSS Annual Meeting Apr 2 nd 2010.
Annual SARs by Study Category, TIR and D: Patterns and Significance Presenter: Charlie Petrosky CSS Annual Meeting Apr 2 nd 2010.
Smolt Monitoring Program: Overview and Data Collection Brandon R. Chockley SMP Pre-Season Meeting February 20,
Oregon State University Real Time Research, Inc. USGS-Oregon Cooperative Fish & Wildlife Research Unit Pre-Management Status of Caspian Tern Colonies in.
Migration pathway, age at ocean entry, and SARs for Snake River Basin fall Chinook prior to summer spill at LGR, LGS, and LMN dams.
Effectiveness of alternative broodstock, rearing and release practices at Winthrop NFH William Gale and Matt Cooper -USFWS, Mid-Columbia River Fishery.
Downstream Survival of Juvenile Stream Type Chinook Salmon and Steelhead Through the Snake/Columbia River Hydropower System and Adult Return Rates AFEP.
Development of Bolt-on Low Profile Overflow / Orifice PIT Tag Antennas for John Day Dam Adult Ladders PTAGIS Field Office Kennewick, Washington November.
2005 Preliminary Summer Spill Data Fall Chinook Radiotelemetry Studies Performed by USGS – BRD, NOAA – NWFSC For the USACE Anadromous Fish Evaluation Program.
Findings of Congress The Endangered Species Act is the last resort for species at risk of extinction. Under the ESA, the National Marine Fisheries Service.
Objective Determine how using 9mm tags may affect our current research project in the John Day Basin.
2005 Subyearling Migration Fish Passage Center. Overview – summer migration Court ordered summer spill occurred from June 20 to August 31, 2005 Question.
Survival and Behavior of Juvenile Chinook Salmon in the Lower Columbia River, Estuary, and Plume G. A. McMichael 1, R. L. McComas 2, J. A. Carter 1, G.
Evaluation of Avian Predation on Juvenile Salmonids in the Columbia River Estuary Donald E. Lyons Ph.D. Candidate Oregon State University Department of.
Upstream passage success rates and straying of returning adults Presenter: Jack Tuomikoski CSS Annual Meeting Apr 2 nd 2010.
Historical Review Fish Migration Data. Two Management Approaches Spill for Fish Passage Planning dates Percent passage dates.
COLUMBIA BASIN KELTS: ABUNDANCE, DOWNSTREAM PASSAGE, AND REPEAT SPAWNING.
Estimated survival of juvenile salmonids through the lower Columbia River and estuary, and estimated mortality from avian predation John Ferguson NOAA.
Proposed PIT Tag Antenna Arrays for Bonneville Dam PH1 Ice and Trash Sluice Way PTAGIS Field Office Kennewick, Washington June 2015.
2016 Smolt Monitoring Program Juvenile Passage Data and
Northwest Fisheries Science Center Technical Management Team
FPAC Development of the Future SMP
Hatchery Subyearling Survival Lower Granite to McNary Dam 1998 to 2007 (preliminary results) Fish Passage Center.
Age at ocean entry of Snake River Basin fall Chinook and its significance to adult returns prior to summer spill at LGR, LGS, and LMN dams.
Comparative Survival Study Project #
Northwest Fisheries Science Center Technical Management Team
Steelhead status in Idaho – 2012 Update
2017 TMT Year-end Review December 12, 2017 Brandon R. Chockley
Roza Dam Evaluation Post Modifications
Direct Survival of Migrating Salmonid Smolts in the Snake and Lower Columbia Rivers: Update with 2007 Results Northwest Power and Conservation Council.
McNary Juvenile Fish Emergency Bypass System
Portland District, USACE
NOAA Mainstem PIT Tag Research
Adult PIT-tag Interrogation System Wells Hydroelectric Project (System Design, Installation and Evaluation)     Shane Bickford* Public Utility District.
Behavior and Survival for Juvenile Salmonids Passing Ice Harbor Dam during reduced and BiOp spill treatments, Gordon Axel, Eric Hockersmith, and.
Smolt Migration 2006 (preliminary results)
Presentation transcript:

Evaluation of prototype fish passage structures in the Lower Granite Dam juvenile fish bypass system – juvenile Pacific lamprey results Rod O’Connor 1, Scott McCutcheon 2, Ryan Richmond 2, and Frank Loge 3 1 Blue Leaf Environmental Ellensburg, WA 3 Department of Civil and Environmental Engineering University of California, Davis Davis, CA 2 Biomark Boise, ID

 In 2013 USACE installed two prototype passage structures in Gatewell 5A at Lower Granite Dam  In 2014 structures were modified  Sharp-crested overflow weir, and  Light ring around 14-inch orifice  Test potential passage improvement measures from gatewell into bypass channel Introduction

Passage structures

 Determine effective collection methods at Lower Granite, Little Goose, and Lower Monumental dams  Evaluate PIT tag retention using two different tagging techniques: surgical methods described by Mesa et al. (2011) and injecting PIT tags with a 16-gauge needle.  Measure travel times through JBS  Including temporary PIT antennas in bypass collection channel in 2014 Objectives

 Fish collected from raceways at JFF  Additional lamprey from LGO and LMN  Release PIT-tagged fishes into Gatewell 5A and bypass collection channel  Passage structures operated one- at-a-time on 24 h cycle  Gatewell residence time  PIT antennas in bypass channel  Travel time from release to first detection at JFF Gatewell 5A Lower Granite JFF

Lower Granite Dam  SMP staff collected fish during daily sample  BLE staff captured individuals passing the separator at night  Most successful collection in the head boxes of raceways with dip net

 8.5 mm L x 1.4 mm Dia PIT  16-gauge needle  n=150 Tag retention with two tag sizes and methods – combined results  “Mesa method”  9 mm L x 2.1 mm Dia PIT  Scalpel incision 2-3 mm  Manually insert PIT  n=150  Control group n=100  All held 96 h  Group tagged with 16-gauge needles had one shed tag  5.3% unhealed tagging wounds  Group tagged with scalpels had two shed tags  36.0% unhealed tag wounds

Yearling Chinook vs. juvenile lamprey travel time  Baseline comparison for juvenile lamprey

2014 Bypass collection channel antenna installation

2014 Bypass Channel PIT array criteria  System design must not require structural modifications to existing collection channel.  Antennas and associated mounting structures must not significantly alter passage conditions of fish.  Antennas must be ‘bolt on’ for safe and easy installation and removal from collection channel.  Antenna dimensions and housing materials must span the area of the collection channel and fit through the entryway to the collection channel.  Corps requirements for hydraulically acceptable antenna design must be met.

“Stick” testing Sticks Detected Sticks Not Detected Proportion detected Chi-Square Statistic TagLocationTotalp-value 12 mmJBS Channel < mmJBS Channel mmJFF Separator mmJFF Separator Live fish detection Species/age classLocation Proportion detected Yearling Chinook JBS Channel0.37 JFF Separator0.99 Juvenile steelhead JBS Channel0.45 JFF Separator0.99 Sub-yearling Chinook JBS Channel0.47 JFF Separator0.99 Lamprey JBS Channel0.12 JFF Separator0.92

Summary Qty tagged and released1, Primary Tag9mm8.4mm Tagging MethodsScalpelInject 16 gauge needle Holding/ReleasePerf buckets/draft tube Collection methodsSMP sort, racewaysSMP sort, raceways, LGR separator screen River flow/run timing“Normal”Bimodal – March and May

Conclusions  Juvenile Lamprey Collection  A combination of SMP daily sample and raceway collection was effective  Lesson learned - start at first indication of lamprey presence – we caught tail end of availability in 2013  Flow regime likely drives availability  Tag retention/tagging methods  Both methods effective  Faster tagging process and fewer unhealed wounds with 16-gauge needle and 8.5 mm PIT  Travel time through the JBS  Median travel times for all treatments were less than salmonid travel times  Detection efficiency with 8.5 mm PIT was lower than 12 mm PIT, especially at temp antennas

Suggestions for future bypass channel studies Install multiple antennas downstream of test gatewells to improve overall detection efficiency of PIT-tag detection system. Multiple antennas will help to mitigate for groups of fish passing through the PIT-tag detection system. Collect system diagnostics without tagged fish in the collection channel to serve as a baseline for system performance. Identify fish release protocol into collection channel to minimize potential for tag collision between groups of released fish and run-at-large PIT-tagged fish.

Acknowledgements Thanks to the following people for providing assistance: USACE: Chris Pinney, David Trachtenbarg, Derek Fryer, Mike Halter, Elizabeth Holdren, Ches Brooks, Bill Spurgeon, Rick Weis, Rich Hilt, all the staff in LGR Project Operations PSMFC: Fred Mensik, Shawn Rapp, Allan Martin, Scott Livingston, Monty Price NOAA: Tiffani Marsh