April 19, 2001
Memorandum
To: Mr. Frank L. Cassidy Jr., Chair
Northwest Power Planning Council
From: ISAB Subcommittee - Chuck Coutant, Lyman McDonald, Dan Goodman,
Dennis Lettenmaier, and Dick Whitney (ISRP)
Re: ISAB consultation recommendations on Council Staff’s Draft Issue
Paper: "Analysis of 2001 Federal Columbia River Power System
Operations on Fish Survival."
At its April 4th meeting, the Council requested an ISAB
review of the Council Staff’s Draft Issue Paper regarding the effects on
ESA-listed fish stocks of an emergency spill elimination in this low-flow
year. The ISAB was requested to have its review completed for the Council’s
April 24 and 25 meeting. This memorandum summarizes the ISAB’s response
to that request.
The ISAB conducted an expedited review process in the form of a
"consultation." A subcommittee of ISAB was established to
conduct this review and participate in discussions with the Council staff.
In a "consultation" we do not attempt to obtain consensus of the
full ISAB, principally because of timing. The subcommittee consisted of
Lyman McDonald, Dan Goodman, and Chuck Coutant, with ad hoc assistance
from Dick Whitney. Dennis Lettenmaier also joined phone discussions. Lyman
and Chuck reviewed two drafts of Bruce Suzumoto's issue paper (March 28
and 30), and prepared comments for Bruce and e-mailed them to him,
followed by a conference call with Bruce on Thursday, April 12. Dick
Whitney was asked to comment on the SIMPAS model (he was also examining it
for ISRP). Subcommittee comments were consolidated after the phone call
with Bruce (who planned to accommodate our thoughts in a revision or
whatever follow-up paper comes from staff) and we drafted bottom lines.
Dan Goodman reviewed our efforts and assisted in preparation of the bottom
lines. The consolidated comments and bottom lines were e-mailed to Council
staff on April 17 in preparation for a conference call on April 18. The
full ISAB was sent the same material and was invited to participate in the
conference call (Dennis Lettenmaier did so). The main product is to be the
outcome of discussions, not a formal report, although we have provided the
bottom lines in this letter.
BOTTOM LINES
1. The SIMPASS model is a spreadsheet with a logical set of
calculations using assumed intermediate survival values, FGEs, etc., for
calculating total juvenile survival of ESA-listed species during
downstream migration through different passage routes and hydropower
projects. As used by both NMFS for the BiOp and by Council staff for these
analyses, it provided a common approach that illustrates the numerical
consequences of particular sets of assumptions.
2. Council staff appear to have used the model in a way that was
mathematically correct, but the reasonableness and applicability of the
results depends on more than this. We recommended sample hand
calculations, which matched the model's calculations reasonably well. We
have no reason to doubt the calculation procedure, but need to stress that
the applicability of the results to a given set of circumstances depends
entirely on the applicability of the assumed input values for those
circumstances. We were not able to confirm the reasonableness of all input
values, however. Most values are extrapolated from a relatively few
scientific studies or are based totally on professional judgment.
3. The focus on ESA-listed stocks leaves questions of non-listed stocks
and biodiversity unanswered, contrary to the thrust of the Council’s
program. The SIMPAS model and the readily available input values do not
consider other species (e.g., sockeye, lamprey) or the potential effects
of either spill reduction or increased transportation on selection for
particular fish stocks that could have long-term effects on species
diversity and diversity of life-history types. Additional analyses may not
be timely, but this drawback of the current results should be
acknowledged.
4. Several aspects of the analysis could be explained better in the
issue paper (or added to the list of caveats) in order to avoid
misunderstandings. These include (1) that the analysis compared a "no
spill/maximum transportation" option with the BiOp recommendations
for spill and transportation in an extreme low water year (not the
normal-year BiOp recommendation), (2) methods for translation of juvenile
survival to adult survival through SARs, (3) the sources of D values that
were used and where the "below Bonneville" point is, (4) sources
of in-river survival rates, and (5) a more thorough description of SIMPAS
model that does not require the reader to search out the BiOp appendix.
These are mostly matters of communication rather than problems with the
analyses, as far as we can tell.
5. Juvenile survival often seems to be the most practical basis for
decision-making for spill and transportation at individual projects,
because SARs are so heavily influenced by large year to year variation in
ocean/estuary survival, and because the sample size of returning adults
often is too small for statistically stable estimation of the SAR. On the
other hand, focus on juvenile survival at the individual project ignores
the possible differences in delayed mortality, and neglects the reality
that we cannot declare a management strategy successful until we have
assurance that the entire resulting life cycle is successful. For this
reason, assessment procedures based on SARs (as the staff analysis
attempted) are preferable whenever a feasible design is available.
6. A clearer basis for prioritizing available water for spill among the
projects would be helpful. Criteria should include biological information
as well as configurations of the projects. Explicit consideration should
be given in this prioritization to the unlisted upriver stocks and those
stocks originating in the lower Columbia tributaries downstream of
collector dams for transportation. We recommend consideration be given in
the prioritization to surface spill opportunities, as discussed in the
ISAB’s recent letter.
7. It would have been useful to have included the Mid-Columbia dams in
the calculations.
8. There is great need to monitor the hydrosystem this year to see if
these estimated survival rates and D values are anywhere near reality. For
example, the scientific studies to compare survival of transported
juveniles to survival of juveniles migrating inriver should be continued.
Monitoring the effects of this low-flow year are so important that we
suggest the Council staff seriously consider requesting additional BPA
funds or selective reprogramming to ensure that this monitoring takes
place. The especially low-flow year offers unique opportunities for
studying fish behavior, survival, and guidance systems when normal
flow-related (often spill-related) migration cues are missing or at low
levels.
9. While the assumptions behind the input values used in the modeling
are consistent with the available data, and are also consistent with
professional judgment of many scientists (they represent committee
consensus), these are only "point estimates" and are subject to
a considerable degree of uncertainty. For this reason, it is not
appropriate to develop a long-range management plan just on the basis of
results from assuming that these uncertain estimates are true. "Best
science" under these circumstances would explore the results from a
range of assumptions corresponding to the range of the uncertainty.
"Best professional judgment" under these circumstances would
recommend a course of action that was predicted to perform acceptably
throughout the range of predicted possible outcomes.
"Precautionary" best professional judgment would be sensitive to
plausible worst cases within the range of predicted possible outcomes.
Although not possible before decisions must be made this year, the
importance of uncertainty in assessments of this type needs to be
evaluated carefully.
We hope that the ISAB subcommittee’s rapid review of the staff’s
drafts and subsequent discussions with the staff have been helpful to them
and that this summary of impressions is useful to the Council.
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