Abstract:
The goal of the Oregon Plan is to restore wild coho and wild steelhead runs. Under the federal
Endangered Species Act, wild coho salmon along the Oregon Coast are listed as Threatened and wild
Oregon Coast steelhead are a candidate for listing. Although cormorants have been hazed at the
Nehalem Estuary for at least 10 years and at the Tillamook and Nestucca Estuaries for at least three
years, spawning ground counts of wild coho salmon, winter steelhead, and fall chinook have averaged
less since hazing began. Thus, hazing does not appear to be useful in recovering wild salmonids.
Hazing is not correlated with consistently improved hatchery returns. The survival of Coded Wire
Tag marked coho smolts at the Nehalem was about the same whether hazing occurred or not, the
percent return for coho smolts was not significantly greater at the hazed Nehalem than at the nonhazed
Salmon River, and the number of returning adult coho salmon was significantly greater with hazing at the
Nehalem hatchery but not at the Trask hatchery in the Tillamook Basin. For winter steelhead, the number
of returning adults to the Nehalem and jacks to the Cedar Creek hatchery in the Nestucca Basin did not
increase significantly with hazing, but the number of jacks returning to the Nehalem did.
Changes in fisheries subsequent to hazing are mixed. Coho catches increased with hazing at
the Nehalem but not at the Tillamook Basin. Nehalem steelhead catches averaged less with hazing, but
chinook fisheries have grown. However, the increase in chinook catches occurred as the number of
wild chinook at spawning areas declined, so the larger catch may be a consequence of a greater harvest
of wild chinook rather than hazing.
Returns may not have increased with hazing because it was ineffective in substantially reducing
predation, because smolts saved by hazing died anyway, or because other factors such as unfavorable
ocean conditions may have been much more important in affecting smolt survival than hazing.
In any case, hazing does not appear to be a panacea for salmonid recovery, and it has costs.
During 1996-1999, the Oregon Legislature spent $100,000 for cormorant hazing, and a biological cost of
hazing is the disturbance of wildlife other than cormorants.
Description:
Executive Summary............ 3
Acronyms .................... 3
Acknowledgments.............. 4
A. Introduction ............. 5
B. Study Areas .............. 5
C. Hazing Methods ........... 7
D. Methods of Counting Cormorants in 1996-1998......................... 11
E. Methods of Correlating Hazing with Salmonid Returns ............ 11
F. Results and Discussion: Smolt Predators and Hazing................... 15
G. Results and Discussion: Wild Salmonid Abundance.................... 20
H. Results and Discussion: Coho CWT Returns...................... 32
I. Results and Discussion: Hatchery Returns...................... 34
J. Results and Discussion: Fisheries Catches...................... 41
K. Concluding Remarks ....... 50
Appendix I. Common and scientific names of animals ..................... 54
Appendix II. Coho, steelhead, and chinook life history information..... 55
Appendix III. Number of coho and winter steelhead smolts released at Nehalem................... 57
Appendix IV. Lack of rigorous controls in testing the effects of hazing ................... 58
Appendix V. Factors other than hazing that can affect salmonid returns.................. 59
Literature Cited ........ 62