Risk Management of Non-target Fish Taxa as Related to Salmon Supplementation Presented by: Gabriel M. Temple.

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Presentation transcript:

Risk Management of Non-target Fish Taxa as Related to Salmon Supplementation Presented by: Gabriel M. Temple

Yakima Program Initial Proposal Central Facility Spring Chinook Summer Steelhead Adult Traps Juvenile Traps Satellite Facility Proposed Production: 7.8 million smolts including Spring, Summer, Fall Chinook, Summer Steelhead, Coho, Sockeye DOE/EA-0392; 1990

Yakima Program Central Facility Acclimation Facility Adult Trap Juvenile Trap Current Production Goal: 810,000 Spring Chinook (*All stock initiative) DOE/EIS-0169; 1996

“Supplementation is the use of artificial propagation in an attempt to maintain or increase natural production while maintaining the long term fitness of the target population, and keeping ecological and genetic impacts on nontarget populations within specified biological limits.” RASP 1992

Supplementation Chronology Building Boundary Baseline Brood Pearsons 2002; Fisheries

NTT Risk Containment Process Identify NTTOC Set Containment Objectives Implement Detection Strategies Identify Changes to NTT Status Determine Causation Adaptive Management Ham and Pearsons 2001

Containment Objectives Pearsons et al. 1998, BPA Report DOE/BP 64878-6 <5% <0% <10% <40% sustainability Containment Objectives

Special thanks: BPA, YN, and WDFW staff Methods….. Special thanks: BPA, YN, and WDFW staff Temple and Pearsons 2007

NTT Risk Containment Process: Sieve Approach 1) Overlap 2) Status 3) Causation Pearsons and Temple 2007

Distribution *

Mainstem O. mykiss Size Clark Flats BACIP ; P=0.33 ANCOVA; P=0.28 (*biomass BACIP; P=0.15)

Tributary O. mykiss Size BACIP; P=0.15 SS model: P=0.004 (Positive)

BACIP Decreased O. mykiss size not attributed to supplementation Abundance may be suppressed in the vicinity of a tributary hatchery release facility relative to reference streams (although we observed population level increases in abundance) Adaptive management (harvest regulation) Pearsons and Temple 2010

Summary Risk management monitoring of NTT is working as planned Currently monitoring the success of management action (harvest regulation) Developing refined methods to evaluate data gaps (remote sensing, PIT technology)

Lessons Learned Pre-implementation planning had bigger influence on ecological interactions than adaptive management monitoring (fine tuning) Sieve approach may not pick up changes of interest (e.g., Teanaway abundance) Value of reference sites/populations (NTT risk monitoring perspective) Adaptive monitoring as information becomes available (e.g., rare dispersed species-PAL, SND, LPD) Containment monitoring can support program from unfounded accusations (e.g., precocious males)