FY 2003 Mainstem/Systemwide proposal 200308100

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Section 1. Administrative

Proposal titleEstablish Relationship between Fish Passage Survival and Turbine Operating Efficiency
Proposal ID200308100
OrganizationNormandeau Associates
Proposal contact person or principal investigator
NameDr. Dilip Mathur
Mailing addressP.O. Box 10, 1921 River Road Drumore, PA 17518
Phone / email7175482121 / dmathur@normandeau.com
Manager authorizing this projectDr. Dilip Mathur
Review cycleMainstem/Systemwide
Province / SubbasinMainstem/Systemwide /
Short descriptionProvide guidance to turbine operators for maximizing passage survival; provide quantitative information for turbine rehabilitation/replacement at dams; and assess whether survival targets are met
Target speciesJuvenile salmonids
Project location
LatitudeLongitudeDescription
45.9365 -119.2966 McNary Dam on the mainstem Columbia River (River Mile 292), Umatilla, Washington
Reasonable and Prudent Alternatives (RPAs)

Sponsor-reported:

RPA
88

Relevant RPAs based on NMFS/BPA review:

Reviewing agencyAction #BiOp AgencyDescription
NMFS Action 88 NMFS The Corps and BPA, in coordination with the Fish Facility Design Review Work Group and the Fish Passage Improvement Through Turbines Technical Work Group, shall continue the program to improve turbine survival of juvenile and adult salmonids.

Section 2. Past accomplishments

YearAccomplishment
2000 Quantified effectiveness of Minimum Gap Runner (MGR) against an existing Kaplan turbine at Bonneville Dam. Narrowing of hub gaps and blade tip gaps improved survival in MGR.
2002 On-going work at McNary Dam to determine the relationship of turbine operating efficiency and fish survival at a single unit (9).
1996 At Rocky Reach Dam, we concluded that no two turbines provide similar fish passage survival conditions and closure of hub gaps can improve survival by 4%.
1995 Estimated survival of simultaneous releases of PIT tagged (NMFS) and balloon tagged (Normandeau) fish at one turbine operating efficiency at Lower Granite Dam. Provided information on interactive effects of turbine efficiency, entrainment depth, and intak

Section 3. Relationships to other projects

Project IDTitleDescription
83 Effect of spill volumes and duration on system survival of juvenile salmonids Add information on in-river survival
102 Avian and pelican predation in reservoirs and tailrace Direct predation immediately upon turbine passage and in-river predation thereafter
103 Avian and pelican predation in reservoirs and tairlace Direct predation immediately upon turbine passage and in-river predation thereafter

Section 4. Budget for Planning and Design phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2003 costSubcontractor
1. Estimation of Direct Effects of Turbine Passage a. Study Design 1 $25,000
1. a. 1 $25,000 Yes
2. Estimation of In-River Post-Passage Survival a. Study Design 1 $25,000
2. a. 1 $50,000 Yes
2. a. 1 $25,000 Yes
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
Outyear budgets for Planning and Design phase

Section 5. Budget for Construction and Implementation phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2003 costSubcontractor
Not Applicable $0
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
Outyear budgets for Construction and Implementation phase

Section 6. Budget for Operations and Maintenance phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2003 costSubcontractor
Not Applicable $0
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
Outyear budgets for Operations and Maintenance phase

Section 7. Budget for Monitoring and Evaluation phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2003 costSubcontractor
1. Estimation of Direct Effects of Turbine Passage b. Fish release and evaluation 3 $1,155,000
1. b. 3 $332,500 Yes
2. Estimation of In-River Post-Passage Survival b. Evaluation and reporting 3 $260,000
2. b. 3 $1,940,000 Yes
2. b. 3 $50,000 Yes
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
Objective 1, Task b 2004 2005 $1,561,875
Objective 1, Task b 2005 2006 $1,639,968
Objective 2, Task b 2004 2005 $2,362,500
Objective 2, Task b 2005 2006 $2,480,625
Outyear budgets for Monitoring and Evaluation phase
FY 2004FY 2005
$3,924,375$4,120,593

Section 8. Estimated budget summary

Itemized budget
ItemNoteFY 2003 cost
Personnel FTE: loaded costs $487,876
Supplies $2,000
Travel Includes meals and lodging $108,754
Indirect $25,000
Subcontractor $1,876,770
Other Balloon tags (9,600@$26 each), Acoustic tags (5,000@$210 each), and Radio tags (500@$175 each) $1,387,100
$3,887,500
Total estimated budget
Total FY 2003 cost$3,887,500
Amount anticipated from previously committed BPA funds$0
Total FY 2003 budget request$3,887,500
FY 2003 forecast from 2002$0
% change from forecast0.0%
Cost sharing
OrganizationItem or service providedAmountCash or in-kind

Reviews and recommendations

This information was not provided on the original proposals, but was generated during the review process.

Recommendation:
Do not fund - no response required
Date:
Aug 2, 2002

Comment:

Not Fundable. This is a proposal to determine if fish passage through turbines is least damaging at peak electrical generating efficiencies of the turbines, which is a commonly held belief that currently guides operations. A sub-objective is to establish whether consistent results are obtained from several turbines at the same dam, under the premise that turbines' effects may differ even when the turbines are nominally similar. The study would determine immediate mortalities and damages at McNary Dam using the proponent's balloon tag, longer-term effects after holding of test fish in tanks, and even longer-term survival of in-river fish tagged with sonic tags (all with appropriate controls released at the base of the dam). The ultimate objective is to establish more scientifically grounded rules for operating turbines for benefit of fish (or for balancing fish survival and power production).

This is a generally well-written proposal from a group with outstanding credentials. There is little doubt that they can achieve what they propose to do. The basic question is whether it is worth investing $12 million to arrive at recommendations that might lead to improvements of 1 to 2% in survival of juvenile salmonids (based on the text and tables at the end of the proposal) that pass through turbines, particularly given the emphasis in the region on measures to divert the juveniles away from the turbine intakes. The question might boil down to an economic one, of how valuable it is to the power operators to be able to diverge from the criterion of operating within 1% of the peak efficiency of turbines? If it is quite valuable, in the millions of dollars, then it ought to be desirable for them to fund this study.

The proposal lacks such estimates of the net benefit to the total population if turbine efficiency were maximized. Turbine survival is currently about 85-95% at most mainstem dams. The installation of improved fish friendly turbines may enhance overall turbine survival rate by maximally 5%, on average. Given that with screen efficiencies as high as 70% or more, spill efficiencies as high as 30% and the use of transportation, it is possible that less than 10% of migrants will ever experience turbine passage in the mainstem FCRPS. Doubling this to 20%, with a turbine mortality improvement of 10% (twice its theoretical potential) provides a net FCRPS system survival increase of about 2%. In reality, we could probably achieve less than 1% with the equipment in place today for Snake River smolts and maybe the same for Columbia River smolts. This would result if we changed out every turbine in the system to a fish friendly design and fine-tuned each operation. The cost of testing the current system at one dam is estimated at $12 million over next 5 years. It appears that as turbines require replacement, there are some energy benefits as well as fish benefits to using more fish friendly turbine designs. It makes great sense to model, test and modify turbines based on previous studies of turbine-induced mortality as new designs are being developed, rather than concentrate on testing existing facilities such as McNary.

The place of this proposal in overall FCRPS planning is not clear. Currently each fish-passage pathway is the focus of intense research that is costing enormous sums. The NMFS Pit Tag data is suggesting that transportation returns more adults from smolts transported high in the system than in river or lower river transports. This database should enable construction of a Decision Support System to establish how many, when and where smolts should be transported, left in river or both depending on river discharge conditions. Turbine passage survival is one component of such a Decision Support System. The question is do we have enough data on hand to build such a model. An independent review panel might evaluate this question from the broader FCRPS perspective.

Aside from economics and FCRPS planning, the proposal does not meet the ISRP review criteria. It is strong on methodology (good science) but short on justification. The technique of balloon tagging has become a staple in hydropower survival studies nationally following patenting of the technique by the proponent. The approach, including the detailed statistical design, is well tested in the Columbia River basin and has been shown to be scientifically sound and fruitful (a useful table of results from many studies in the basin is included at the end). The novelty of this study is the inclusion of more than one turbine (to evaluate consistency of results) and longer-term, in-river survival (a topic for which the balloon tag work is often criticized). The study objectives, tasks and methods are described in adequate detail. However, the justification for this study is brief and incomplete. The study would be very expensive, and thus a more thorough scientific justification is mandatory. The previous studies are not well summarized to demonstrate that this proposal is the next logical step in obtaining more successful fish-passage. How much change in fish survival and electricity generation are we talking about in shifting from the peak efficiency level (large amounts, small amounts)? That is, what level of biological benefit (an ISRP review criterion) is at stake? What evidence is there now that adjacent turbines differ in their performance? What literature suggests that in-river mortality may be higher than indicated by the immediate or short-term effects shown by the balloon tag (and by how much)? The relationships of the proposed work to previous or on-going studies are given briefly and very generally (what are the project numbers listed in Part I?). The RPA's from the NMFS BiOp are listed, but neither named nor discussed as justification for this work. No priorities from the mainstem/systemwide province solicitation or program summary are mentioned. There is no mention of the Council's Fish and Wildlife Program, for which the ISRP must determine if the proposal is consistent. The whole project is considered one of "monitoring and evaluation" but the proposal would have benefited from a short discussion of how any operational changes implemented as a result of this study would be monitored and evaluated short of redoing this whole study.

In summary, the proposal falls short of meeting the ISRP review criteria. This is particularly true for the criterion of demonstrating likely biological benefit. With very high costs, a favorable cost-to-biological-benefit ratio is not evident.

The proposal was not selected by the Action Agency/NMFS RME Work Group for RME review.


Recommendation:
Do Not Fund
Date:
Oct 24, 2002

Comment:

Major survival benefits from this project are doubtful. This project would be more appropriately funded in the Corps of Engineers AFEP program.
Recommendation:
Do Not Fund
Date:
Nov 5, 2002

Comment:

Do Not Fund; agree with CBFWA. This is a proposal to determine if fish passage through turbines is least damaging at peak electrical generating efficiencies of the turbines, which is a commonly held belief that currently guides operations. A sub-objective is to establish whether consistent results are obtained from several turbines at the same dam, under the premise that turbines' effects may differ even when the turbines are nominally similar. The study would determine immediate mortalities and damages at McNary Dam using the proponent's balloon tag, longer-term effects after holding of test fish in tanks, and even longer-term survival of in-river fish tagged with sonic tags (all with appropriate controls released at the base of the dam). The ultimate objective is to establish more scientifically grounded rules for operating turbines for benefit of fish (or for balancing fish survival and power production).

This is a generally well-written proposal from a group with outstanding credentials. There is little doubt that they can achieve what they propose to do. The basic question is whether it is worth investing $12 million to arrive at recommendations that might lead to improvements of 1 to 2% in survival of juvenile salmonids (based on the text and tables at the end of the proposal) that pass through turbines, particularly given the emphasis in the region on measures to divert the juveniles away from the turbine intakes. The question might boil down to an economic one, of how valuable it is to the power operators to be able to diverge from the criterion of operating within 1% of the peak efficiency of turbines? If it is quite valuable, in the millions of dollars, then it ought to be desirable for them to fund this study.

Aside from economics and FCRPS planning, the proposal does not meet the ISRP review criteria. It is strong on methodology (good science) but short on justification. The technique of balloon tagging has become a staple in hydropower survival studies nationally following patenting of the technique by the proponent. The approach, including the detailed statistical design, is well tested in the Columbia River basin and has been shown to be scientifically sound and fruitful (a useful table of results from many studies in the basin is included at the end). The novelty of this study is the inclusion of more than one turbine (to evaluate consistency of results) and longer-term, in-river survival (a topic for which the balloon tag work is often criticized). The study objectives, tasks and methods are described in adequate detail. However, the justification for this study is brief and incomplete. The previous studies are not well summarized to demonstrate that this proposal is the next logical step in obtaining more successful fish-passage. How much change in fish survival and electricity generation are we talking about in shifting from the peak efficiency level (large amounts, small amounts)? That is, what level of biological benefit (an ISRP review criterion) is at stake? What evidence is there now that adjacent turbines differ in their performance? What literature suggests that in-river mortality may be higher than indicated by the immediate or short-term effects shown by the balloon tag (and by how much)? The relationships of the proposed work to previous or on-going studies are given briefly and very generally (what are the project numbers listed in Part I?). The RPA's from the NMFS BiOp are listed, but neither named nor discussed as justification for this work. No priorities from the mainstem/systemwide province solicitation or program summary are mentioned. There is no mention of the Council's Fish and Wildlife Program, for which the ISRP must determine if the proposal is consistent. The whole project is considered one of "monitoring and evaluation" but the proposal would have benefited from a short discussion of how any operational changes implemented as a result of this study would be monitored and evaluated short of redoing this whole study.

In summary, the proposal falls short of meeting the ISRP review criteria. This is particularly true for the criterion of demonstrating likely biological benefit, which is slight. It might be better justified as a hydropower proposal.


Recommendation:
Date:
Jan 21, 2003

Comment:

Statement of Potential Biological Benefit
Benefits are indirect. The research would try to determine whether passage survival through multiple turbines at McNary are the same and whether the point of peak operating efficiency is correlated with peak fish survival.

Comments
This proposal is redundant. The Corps did this last year (2002 field season) and the results should be available soon. The Corps used radio tags instead of acoustics. Using acoustic tags for indirect survival has not been proven and will need to be developed, which could be costly. NOAA Fisheries believes there needs to be an accuracy of plus or minus 2 percent (not a 3 percent allowance that is in the proposal). Increasing the accuracy would also increase the cost of the proposal.

Already ESA Required?
No

Biop?
Yes


Recommendation:
Do Not Fund (Tier 3)
Date:
Jun 11, 2003

Comment:

Category:
3. Other projects not recommended by staff

Comments: