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Survival of Downstream MigrationNational Marine Fisheries ServiceDecember 21, 2000 |
Average | Best Year | Worst Year | |||||||
---|---|---|---|---|---|---|---|---|---|
In sequence heading downstream | Sub-Yearling Chinook (1995-99) | Yearling Chinook (1994-99) | Steelhead (1994-99) | Sub-Yearling Chinook (1995) | Yearling Chinook (1999) | Steelhead (1995) | Sub-Yearling Chinook (1997)1 | Yearling Chinook (1994) | Steelhead (1994) |
Lewiston, Idaho | 1,000 | 1,000 | 1,000 | 1,000 | 1,000 | 1,000 | 1,000 | 1,000 | 1,000 |
Lower Granite Pool | 600 | 959 | 953 | 709 | 967 | 967 | 375 | 967 | 927 |
Dam | 565 | 933 | 929 | 668 | 941 | 944 | 353 | 936 | 900 |
Little Goose Pool | 454 | 872 | 880 | 631 | 908 | 863 | 212 | 797 | 803 |
Dam | 428 | 858 | 850 | 595 | 894 | 839 | 200 | 777 | 760 |
Lower Monumental Pool | 366 | 810 | 823 | 503 | 870 | 839 | 136 | 704 | 729 |
Dam | 345 | 768 | 777 | 473 | 827 | 797 | 129 | 658 | 678 |
Ice Harbor Pool | 287 | 721 | 720 | 424 | 806 | 755 | 84 | 598 | 628 |
Ice Harbor Dam | 281 | 704 | 705 | 415 | 786 | 739 | 82 | 586 | 615 |
McNary Pool | 221 | 658 | 653 | 360 | 769 | 702 | 46 | 517 | 557 |
Dam | 212 | 641 | 637 | 340 | 748 | 684 | 45 | 502 | 543 |
John Day Pool | 139 | 548 | 562 | 263 | 658 | 620 | 16 | 400 | 452 |
Dam | 133 | 532 | 547 | 251 | 638 | 605 | 15 | 388 | 441 |
The Dalles Pool | 115 | 509 | 524 | 232 | 627 | 587 | 11 | 361 | 417 |
Dam | 102 | 463 | 476 | 205 | 570 | 533 | 10 | 328 | 379 |
Bonneville Pool | 79 | 427 | 440 | 176 | 553 | 503 | 5 | 287 | 340 |
Bonneville Dam | 74 | 403 | 415 | 165 | 519 | 473 | 5 | 272 | 322 |
Direct Mortality Lower Snake River 4 Dams & 4 Pools | 72% | 30% | 29% | 58% | 21% | 26% | 92% | 41% | 38% |
Direct Mortality Columbia River 4 Dams & 4 Pools | 21% | 30% | 29% | 25% | 27% | 26% | 8% | 32% | 29% |
Direct Mortality Combined 8 Dams & 8 Pools | 93% | 60% | 58% | 83% | 48% | 52% | 99% | 73% | 68% |
Mortality of 8 Dams | 12% | 20% | 17% | 18% | 23% | 21% | 5% | 18% | 22% |
Mortality of 8 Pools2 | 81% | 40% | 41% | 65% | 25% | 31% | 95% | 54% | 47% |
Indirect Mortality
occurring later in life from the effects of 8 Pools & 8 Dams | ? | ? | ? | ? | ? | ? | ? | ? | ? |
Sub-Yearling Chinook | Yearling Chinook | Steelhead | Sub-Yearling Chinook | Yearling Chinook | Steelhead | Sub-Yearling Chinook | Yearling Chinook | Steelhead | |
Average | Best Year | Worst Year |
CAVEAT: Sub-yearling data has been called into question following this publication in 2000.
More caveats discussed in Appendix D of FCRPS 2000 Biological Opinion.
Red indicates 10% mortality or more
Dam survival is modeled and Pool survival is calculated by subtraction from empirical data.
Draft 2000 FCRPS Biological Opinion, Appendix B
Data Reformatted from Tables B-7 through B-23
& Updated by Final 2000 FCRPS BiOp Table 6.2-7
1No Data available for 1994 Sub-Yearling Chinook. Sub-Yearling Chinook are typically Fall Chinook while Yearling Chinook are typically Spring/Summer Chinook
2No Data is available for mortality/survivability before dams were built but it was certainly much less than the current mortality.
Best professional judgement was used to develop some of the passage parameters, e.g., in some cases, fish passage data gathered at one dam during a single passage season was applied to several other similar hydrosystem projects.
Reach survival data is limited to NMFS PIT tag data collected during 1994-99. These years represent a range in flow and environmental conditions. In several years, reach survival data were extrapolated from some of the upper projects in the Snake River (on a per-mile basis) to the entire system. The reach survival estimates are point estimates roughly classified by the volume of runoff during the year in which the data were collected.
Although there may be uncertainty about the accuracy of the resulting pool and dam survival estimates, the BET and NMFS found that the model output for the years 1994-99 was reasonable and produced reach survival estimates similar to the empirical estimates. Once the model was calibrated to data for the current operation, the BET and NMFS considered it had a reasonable base case from which to make comparisons of additional model studies over a range of water conditions represented by water years 1994-99 of potential future juvenile fish passage actions.
Caveats of methodology:
Related Links:
Columbia Basin Salmon Recovery Strategy
Previously posted table based on Draft BiOp 7/27/00 Appendix B
FCRPS 2000 Biological Opinion (rather large at 21.4 megabytes)
Appendix D FCRPS 2000 Biological Opinion
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