FY 2003 Mainstem/Systemwide proposal 200308400

Additional documents

TitleType
35028 Narrative Narrative
35028 Powerpoint Presentation Powerpoint Presentation
35028 Sponsor Response to the ISRP Response
Sturgeon Overview Powerpoint Presentation

Section 1. Administrative

Proposal titleEvaluate White Sturgeon Nutritional Needs & Contaminant Effects Influenced by the Hydroelectric System
Proposal ID200308400
OrganizationPortland State University (PSU)
Proposal contact person or principal investigator
NameEugene Foster
Mailing addressP.O. Box 751 Portland, OR 97207-0751
Phone / email5032295358 / [email protected]
Manager authorizing this project
Review cycleMainstem/Systemwide
Province / SubbasinMainstem/Systemwide /
Short descriptionEvaluate the effects of the hydroelectric system on white sturgeon nutritional needs and contaminant effects that would be used in white sturgeon management decisions for the mitigation and restoration of Columbia River white sturgeon populations.
Target speciesWhite Sturgeon
Project location
LatitudeLongitudeDescription
45.7 -120.41 Columbia River from the mouth to Priest Rapids Dam.
Reasonable and Prudent Alternatives (RPAs)

Sponsor-reported:

RPA

Relevant RPAs based on NMFS/BPA review:

Reviewing agencyAction #BiOp AgencyDescription

Section 2. Past accomplishments

YearAccomplishment
1996 Developed and employed methodologies for the analysis of gonad tissue from white sturgeon for toxic chemicals.
1997 Developed and employed methodologies for the analysis of liver tissue from whiet sturgeon for toxic chemical analysis.
2000 Developed and employed methodologies for the quantification of important steroid metabolizing enzymes in white sturgeon.
2001 Found that DDE, DDD, and DDT were the most frequently detected chlorinated pesticides in livers of Columbia River white sturgeon with DDE>DDD>DDT.
2001 Found that plasma androgens were negatively correlated with liver DDE in male white sturgeon from the Columbia River.
2001 Found that liver enzymes were elevated in white sturgeon from Bonneville and The Dalles Pools.
2001 Found irregular ovarian development in several female white sturgeon from the Columbia River.
2002 Found PCBs were frequently detected in liver and gonads of Columbia River white sturgeon
2002 Found that PCBs, DDE, DDD, and DDT concentrations were highest in gonad<liver<cheek in samples of Columbia River white sturgeon.
2002 Found that white sturgeon steroid metabolizing enzymes were higher in livers with higher concentrations of toxic chemicals.
2002 Found elevated levels of plasma vitellogenin in Columbia River white sturgeon indicating exposure to endocrine disrupting type chemicals.
2002 Found altered Columbia River white sturgeon gonad and liver histology consistent with exposure and effects from toxic chemicals.
2002 Found reduced Columbia River white sturgeon condition factor and nutritional status that was associated with elevated levels of PCBs and chlorinated pesticides.

Section 3. Relationships to other projects

Project IDTitleDescription
198605000 White Sturgeon Mitigation and Restoration in the Columbia and Snake Rivers Upstream from Bonneville Dam Coordination of Project SturgnGro with Project 198605000 for obtaining young of year and juvenile white sturgeon samples from the sampling efforts conducted under Project 198605000.

Section 4. Budget for Planning and Design phase

Task-based budget
ObjectiveTaskDuration in FYsEstimated 2003 costSubcontractor
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
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
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. Determine if foods currently consumed by YOY (<25cm), juvenile (25 - 108cm) and legal size (109 - 150cm) white sturgeon are meeting their nutritional needs. a. Perform taxonomic identification and measure the caloric value of the stomach contents and nutritional status of YOY, juvenile, and legal size white sturgeon from below Bonneville Dam, Bonneville, The Dalles, John Day, McNary Pools. Ongoing $129,061
2. Determine if reproductively immature white sturgeon are adversely affected by contaminants influenced by the hydroelectric system. a.Measure PCB, chlorinated pesticides and other bioaccumlative toxic chemicals in sediments and the stomach contents and tissues of legal size; and trace elements and essential elements in tissues of YOY, JUV, LEG white sturgeon from Objective 1. Ongoing $188,840 Yes
2. b. Measure biological endpoints indicative of adverse effects from exposure to toxic chemicals in LEG white sturgeon from Objective 2a. Ongoing $138,340
Outyear objectives-based budget
ObjectiveStarting FYEnding FYEstimated cost
1. Determine if foods currently consumed by YOY, juvenile and legal size white sturgeon are meeting their nutritional needs. 2004 2005 $168,616
2. Determine if reproductively immature white sturgeon are adversely affected by contaminants influenced by the hydroelectric system. 2004 2005 $413,469
Outyear budgets for Monitoring and Evaluation phase
FY 2004FY 2005
$388,696$219,389

Section 8. Estimated budget summary

Itemized budget
ItemNoteFY 2003 cost
Personnel FTE: PSU = $37,256 (2 GRA 0.45 FTE, 1 RA 0.5 FTE) OSU = $42,523 (1 RA 1.0 FTE, 1 RA 0.08 FTE) $79,779
Fringe PSU = $7,967 OSU = $19,135 $27,102
Supplies PSU = $16,046 OSU = $12,311 $28,357
Travel PSU = $5,500 OSU = $5,500 $11,000
Indirect PSU (42%) = $34,450 PSU (42% 1st $25K for contracts) = $36,540 OSU (41.5%) = $31,481 $102,471
Capital PSU = $20,000 (fluorometric microtiter plater reader) $20,000
NEPA 0 $0
Subcontractor Lab for PCB & OC analysis ($171,532), Lab for PCDD/PCDF analysis ($6,000), P450 Lab ($10,000) $187,532
$456,241
Total estimated budget
Total FY 2003 cost$456,241
Amount anticipated from previously committed BPA funds$0
Total FY 2003 budget request$456,241
FY 2003 forecast from 2002$0
% change from forecast0.0%
Cost sharing
OrganizationItem or service providedAmountCash or in-kind
DEQ Personnel time $31,500 in-kind
ODFW Personnel time for fish collection $0 cash
USGS Personnel time for fish collection $0 cash

Reviews and recommendations

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

Recommendation:
Fundable only if response is adequate
Date:
Aug 2, 2002

Comment:

A response is needed. This is a basic research study to try to unravel the mystery of why white sturgeon recruitment is low to non-existent in Columbia River reservoirs. Earlier studies have indicated potential impacts of certain contaminants on fish condition and certain physiological indicators that could suggest adverse effects on growth and reproduction of white sturgeon in Bonneville Pool. The proposal seeks to build upon this work by determining if food consumed by sturgeon is meeting their nutritional needs and if immature fish are being adversely affected by contaminants, particularly in their food.

This is a thorough, basic research proposal that generally meets the ISRP review criteria, although there are several technical questions that need elaboration in a response (see below). The topic is of regional interest, and the proposal shows how it is included in the FWP, Action Agencies' Implementation Plan, Mainstem Solicitation, and the Sturgeon Program Summary. The background section gives up-to-date details of prior work on the subject, including data. The objectives and tasks are fairly clear, and the planned methods (including sample sizes) are laid out in detail. There is a qualified staff, and they have demonstrated their capability to do the work with prior studies funded elsewhere. The study is highly contaminant oriented, and food and feeding are given attention mainly through analysis of stomach contents. There might have been a more ecological flavor.

There are two general difficulties with this sort of work. First, knowing with some certainty that changes in physiological and biochemical indicators will translate into biologically meaningful reductions in growth and reproduction and second, knowing with some certainty that the changes in physiological and biochemical indices that are observed are a direct consequence of exposure to contaminants and not a result of some other environmental factors (e.g., changes in flow regime, temperature) or a density-related phenomenon. The sponsors need a better justification of the ecological consequences of the research if it is to be useful to managers. The proposal also lacks clear, mechanistic hypotheses and methods for data analysis that are specific to testing these hypotheses. Several elements of the proposal need to be expanded. For example, objective 1, Task 1a purports to determine if food consumed by sturgeon are meeting their nutritional needs. Stomach contents and caloric value of the stomach contents will be assessed. Exactly how will the information gained from stomach contents and caloric value be used to determine if the nutritional needs are being met? How will nutritional status be assessed? How will the "relationship between stomach contents, caloric content, and nutritional status" (page 13) be assessed and what will it mean?

Objective 2 purports to measure contaminant levels in sediments, stomach contents, and fish tissues and to use this information to assess the association between nutritional status and contaminant concentration, and to use sediment and water chemistry to evaluate locational differences and associations with tissue chemistry. How will this be done? What type of analysis will be employed? Task 2b asserts that biological endpoints (e.g., CF, GSI) indicative of adverse effects will be measured. A better justification of the validity of these endpoints as indicators of adverse effects is needed. For example, what is an "adverse effect" and how much does an endpoint such as CF or GSI need to be reduced before an adverse effect occurs? How will the information gathered in this research be used to assess adverse effects on maturing sturgeon? Overall, most of the methods lack sufficient conceptual detail to convince a reviewer that the research will accomplish what it proposes. It is unclear how much new knowledge relevant to restoration and protection of sturgeon will be generated by this research beyond what is already known from past studies. These difficulties need to be addressed in a response.

This project was not selected by the Action Agency/NMFS RME Work Group for additional review.


Recommendation:
Recommended Action
Date:
Oct 24, 2002

Comment:

Although the hydropower system has exacerbated the contaminant problem, it is not solely responsible. Significant cost share from contaminant sources would seem appropriate.
Recommendation:
Fund
Date:
Nov 5, 2002

Comment:

Fundable at a low priority. We agree with the CBFWA review and "Recommended Action" ranking. This is a basic research study to try to unravel the mystery of why white sturgeon recruitment is low to non-existent in Columbia River reservoirs. Earlier studies have indicated potential impacts of certain contaminants on fish condition and certain physiological indicators that could suggest adverse effects on growth and reproduction of white sturgeon in Bonneville Pool. The proposal seeks to build upon this work by determining if food consumed by sturgeon is meeting their nutritional needs and if immature fish are being adversely affected by contaminants, particularly in their food.

This thorough proposal generally meets the ISRP review criteria, although there were several technical questions that needed elaboration. The response elaborated, but did little to clarify the ISRP's questions. The ISRP requested a better justification of the ecological consequences of the research if it is to be useful to managers.

The topic is of regional interest, and the proposal shows how it is included in the FWP, Action Agencies' Implementation Plan, Mainstem Solicitation, and the Sturgeon Program Summary. The background section gives up-to-date details of prior work on the subject, including data. The objectives and tasks are fairly clear, and the planned methods (including sample sizes) are laid out in detail. There is a qualified staff, and they have demonstrated their capability to do the work with prior studies funded elsewhere. The study is highly contaminant oriented, and food and feeding are given attention mainly through analysis of stomach contents. There might have been a more ecological flavor.

There are two general difficulties with this sort of work. First, knowing with some certainty that changes in physiological and biochemical indicators will translate into biologically meaningful reductions in growth and reproduction and second, knowing with some certainty that the changes in physiological and biochemical indices that are observed are a direct consequence of exposure to contaminants and not a result of some other environmental factors (e.g., changes in flow regime, temperature) or a density-related phenomenon. The response did little to assuage our concerns on these points.

Overall, most of the methods lack sufficient conceptual detail to convince a reviewer that the research will accomplish what it proposes. It is unclear how much new knowledge relevant to restoration and protection of sturgeon will be generated by this research beyond what is already known from past studies.


Recommendation:
Date:
Jan 21, 2003

Comment:

Comments
Not Reviewed

Already ESA Required?

Biop?
No


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

Comment:

Category:
3. Other projects not recommended by staff

Comments: