FY07-09 proposal 200300600
Jump to Reviews and Recommendations
Section 1. Administrative
Proposal title | Effectiveness Monitoring of Estuary Restoration in the Grays River and Chinook River Watersheds |
Proposal ID | 200300600 |
Organization | Columbia River Estuary Study Taskforce (CREST) |
Short description | This project will evaluate the effectiveness of a suite of estuary restoration projects in the Grays River and Chinook River watersheds. |
Information transfer | |
Proposal contact person or principal investigator |
Contacts
Contact | Organization | |
---|---|---|
Form submitter | ||
Robert Warren | Columbia River Estuary Study Taskforce | rwarren@columbiaestuary.org |
All assigned contacts | ||
Ian Sinks | Columbia Land Trust | isinks@columbialandtrust.org |
Robert Warren | Columbia River Estuary Study Taskforce | rwarren@columbiaestuary.org |
Robert Warren | Columbia River Estuary Study Taskforce | rwarren@columbiaestuary.org |
Section 2. Locations
Province / subbasin: Columbia Estuary / Columbia Estuary
Latitude | Longitude | Waterbody | Description |
---|---|---|---|
N 46 18' 13.2" | W 123 57' 55.8" | Chinook River | Lower reaches of the Chinook River. |
N 46 18' 29.1 | W 123 41' 3.3 | Grays River | Lower tidally influenced reaches of the Grays River |
Section 3. Focal species
primary: Chinook Lower Columbia River ESUprimary: Chum Columbia River ESU
primary: Coho Lower Columbia River ESU
secondary: Coastal Cutthroat Southwest Washington/Columbia River ESU
secondary: Other Anadromous
secondary: Resident Fish
Section 4. Past accomplishments
Year | Accomplishments |
---|---|
2005 | Initiated prey resource and utilization components above and below the existing tide gate structure and trap netting in an adjacent reference/comparision site |
2004 | Established length of residence (and associated growth rates) for hatchery and natural origin salmonids in the lower Chinook River and Estuary; documented timing and magnitude of juvenile migration events; and documented seasonal variation in WQ parameter |
2003 | Initiated all project elements including deployment of water quality instruments, operation of rotary screw migrant traps, and lower river seining |
Section 5. Relationships to other projects
Funding source | Related ID | Related title | Relationship |
---|---|---|---|
BPA | 200301000 | Historic Hab Food Web Link Sal | Collaborative effort to evaluate estuary restoration in the Grays River |
Other: NFWF | 2005-0127-003 | Columbia River estuary wetland restoration and monitoring: Youngs Bay, Oregon and Baker Bay, Washington | Similar monitoring approach for estuary restoration projects in Oregon and Washingon |
BPA | 200301100 | Columbia R/Estuary Habitat | Significant contributor to restoration of sites to be monitored |
Other: USACE | na | Movements of coastal cutthroat trout in the lower Columbia River: tributary, mainstem, and estuary use | Collaboration with respect to PIT tagging and PIT tag detection in the Chinook River |
Section 6. Biological objectives
Biological objectives | Full description | Associated subbasin plan | Strategy |
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Section 7. Work elements (coming back to this)
Work element name | Work element title | Description | Start date | End date | Est budget |
---|---|---|---|---|---|
Manage and Administer Projects | Manage project implementation and completion | Manage project jointly between CREST and CLT | 10/1/2007 | 9/30/2009 | $46,296 |
Biological objectives |
Metrics |
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Produce Annual Report | Complete annual reports | Project managers and biologist will develop comprehensive report of monitoring findings. | 7/1/2007 | 9/30/2009 | $13,335 |
Biological objectives |
Metrics |
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Produce Status Report | Complete project status reports | Status reports will be submitted quarterly | 10/1/2006 | 7/30/2009 | $4,666 |
Biological objectives |
Metrics |
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Collect/Generate/Validate Field and Lab Data | Analyze fall out trap and bentic core samples | Analysis to be performed by UW WET. | 6/1/2007 | 9/30/2009 | $67,650 |
Biological objectives |
Metrics |
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Collect/Generate/Validate Field and Lab Data | Analyze stomach content samples from juvenile salmon | Analysis will be performed by UW WET - 1050 total samples anticipated | 6/30/2007 | 9/30/2009 | $94,500 |
Biological objectives |
Metrics |
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Collect/Generate/Validate Field and Lab Data | Capture and process juvenile salmon | Using rotary screw migrant trap, fyke nets, and beach seine to capture and process juvenile salmon in migration corridors (Chinook and Grays) restoration sites, and reference sites twice monthly at 5 sites. | 10/1/2006 | 9/30/2009 | $232,774 |
Biological objectives |
Metrics |
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Collect/Generate/Validate Field and Lab Data | Collect stomach content samples from juvenile salmon and invertebrates from sample sites | A representative subset of all species of captured salmon will provide stomach content sample via non-lethal gastric lavage. Invertebrates will also be collected using fall out traps and benthic cores. | 10/1/2006 | 9/30/2009 | $22,539 |
Biological objectives |
Metrics |
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Create/Manage/Maintain Database | Manage database to house all collected data | Create and maintain database to house all project data | 10/1/2006 | 9/30/2009 | $10,078 |
Biological objectives |
Metrics |
Section 8. Budgets
Itemized estimated budget
Item | Note | FY07 | FY08 | FY09 |
---|---|---|---|---|
Personnel | [blank] | $85,216 | $85,216 | $85,216 |
Supplies | [blank] | $4,500 | $4,500 | $4,500 |
Other | Sample Processing | $53,550 | $53,550 | $53,550 |
Travel | [blank] | $3,492 | $3,492 | $3,492 |
Overhead | [blank] | $17,188 | $17,188 | $17,188 |
Totals | $163,946 | $163,946 | $163,946 |
Total estimated FY 2007-2009 budgets
Total itemized budget: | $491,838 |
Total work element budget: | $491,838 |
Cost sharing
Funding source/org | Item or service provided | FY 07 est value ($) | FY 08 est value ($) | FY 09 est value ($) | Cash or in-kind? | Status |
---|---|---|---|---|---|---|
TBD | Personnel | $20,000 | $20,000 | $20,000 | Cash | Under Development |
Totals | $20,000 | $20,000 | $20,000 |
Section 9. Project future
FY 2010 estimated budget: $165,000 FY 2011 estimated budget: $165,000 |
Comments: Continuation of long-term monitoring project of restoring estuary restoration sites |
Future O&M costs:
Termination date: 2009
Comments:
Final deliverables: Comprehensive scientific report of project findings.
Section 10. Narrative and other documents
20030600n-2 | Jul 2006 |
Devil's elbow 05-06 | Jul 2006 |
Reviews and recommendations
FY07 budget | FY08 budget | FY09 budget | Total budget | Type | Category | Recommendation |
---|---|---|---|---|---|---|
NPCC FINAL FUNDING RECOMMENDATIONS (Oct 23, 2006) [full Council recs] | ||||||
$0 | $0 | $0 | $0 | Expense | ProvinceExpense | Do Not Fund |
NPCC DRAFT FUNDING RECOMMENDATIONS (Sep 15, 2006) [full Council recs] | ||||||
$0 | $0 | $0 | $0 | ProvinceExpense | ||
Comments: OR and WA same |
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NPCC DRAFT FUNDING RECOMMENDATIONS (Sep 15, 2006) [full Council recs] | ||||||
$0 | $0 | $0 | $0 | ProvinceExpense | ||
Comments: OR and WA same |
ISRP PRELIMINARY REVIEW (Jun 2, 2006)
Recommendation: Response requested
NPCC comments: Although there is solid justification for this work, the proposal requires improvement in several areas. In particular, the sponsors need to provide a better explanation of past accomplishments, organized by objective in the original proposal, and a far better explanation of objectives and methods. The proponents need to provide further information on study sample sites relative to the restoration projects shown in Table 1 and how the sample sites were chosen, status of the tide gate restoration initiative (slated for removal in 2006), and evidence that annual reports are being made available. The technical background is adequate and the rationale for the project is clearly defined. The project seeks to continue monitoring the effectiveness of restoration projects in the Chinook River and to begin monitoring in the Grays River. Rationale and significance to subbasin plans and regional programs: The proposal clearly addresses elements of the lower Columbia estuary subbasins plans and the Plan for Research, Monitoring, and Evaluation of Salmon in the Columbia River Estuary. It also is related to a number of RPA’s in the 2000 Biological Opinion. The Grays River and Chinook River estuary complex is important in that it is potentially available to all juvenile salmonids rearing in or moving through the lower Columbia River estuary. Relationships to other projects: The sponsors will continue to collaborate with University of Washington researchers working in the estuary complex at the Grays River mouth (project #20030100). The two projects seem to be well integrated, and the current proposal almost provides a service function to #20030100. The project appears to have excellent collaborative relationships with CREST and a number of federal and state agencies and private entities. The collaboration includes data sharing, consistency of methods, and joint participation in projects. Project history: A good set of baseline data has been obtained on juvenile salmon ecology but the information has not been published and is still considered preliminary by the proponents. The sponsors need to summarize results by objective in the original proposal to enable evaluation of how well each objective was accomplished. The sponsors also need to explain the results presented in the Tables and Figures. What is the data telling us? What conclusions can be drawn at this point? Do the tables and figures provide all data collected to date? What has been learned about pre-restoration baseline conditions? One problem with the original design of the work is that a specific tide gate has not been modified to increase flooding in the Chinook River estuary. The proposal states one out of three gates will be engineered in April 2006. The proposal does not state if this will provide sufficient water exchange to satisfy the original goal. Objectives: The sponsors need to provide a much better explanation of objectives. Obtaining baseline data on juvenile salmon ecology (residency, feeding, apparent growth) is a measurable objective. Benefits to salmon from restoration activities are more difficult to quantify and were not mentioned in the proposal. Will any of the work from the original proposal be continued such as the monitoring work in the Chinook? If so, what are the objectives and methods? What is the rationale for selecting the Grays River sites? What were the pre-restoration baseline conditions? When were restoration actions taken and what were they? Have any data been obtained so far at these sites? A better explanation of the reference sites and why they were chosen is needed. Tasks (work elements) and methods: Most of the methods appear adequate for accomplishing the objectives. Several questions, however, need to be addressed. More detail is required on sampling locations and rationale for their choice. How frequently will sampling occur? How will the sponsor decide which type of tagging to employ? The trapping methods are adequate. The sponsors state that the scale samples will be analyzed, if possible. The sponsors need to assure that the scales will be analyzed. The scales will provide critical information on age and life history and will be important in assessing life history diversity. How will the data be analyzed? After several years of data collection, the sponsor should be able to adequately address the question of data analysis. The request to continue sampling until 2013 when an apparent dynamic equilibrium is established is not supported by any scientific rationale -only a quote from "some researchers". The proponents should explain what they mean by a "dynamic equilibrium" and how it will be evidenced. Monitoring and evaluation: The purpose of the proposal is effectiveness monitoring. However, there are so many uncertainties related to project objectives and past accomplishments that it is difficult to determine whether the project will be a viable M&E. The proponents state that an additional seven years of monitoring is required. A rationale for this time frame is required. Facilities, equipment, and personnel: Facilities and equipment are adequate. The supervisory personnel do not have extensive experience in reporting. Information transfer: To date, the information from the project has not been widely disseminated, presumably because the proponents view the data as preliminary. Some data sharing has occurred with University of Washington researchers. The proposal states that annual reports are prepared but they are not cited. A database is being maintained by CREST. Benefits to focal species: An evaluation of the restoration projects in the lower Columbia River estuary will benefit focal species especially fall chinook and chum. The benefits will be sustained in the long term, but periodic monitoring will be required for the engineered restoration projects (e.g., will the tide gate continue to allow access by fish?) Benefits to non-focal species: Habitat restoration should benefit non-focal species. It is not clear if endangered biota besides salmon will be affected by the flooding of restored areas. Trapping in the river could affect non-focal fish species and mammals if precautions are not taken.
ISRP FINAL REVIEW (Aug 31, 2006)
Recommendation: Not fundable
NPCC comments: The sponsors did not provide a systematic and explicit response to the ISRP's comments. Instead, they submitted a revised proposal that was only marginally improved over the original proposal. They provided more data describing results but very little interpretation as requested by ISRP. Although the sponsors organized the results of past work (project history) according to the objectives of the original proposal as the ISRP recommended, the results should have been better explained. The sponsors simply re-iterated the results of their baseline data gathering but did not add any further interpretation or show how the data would be used to evaluate success or failure of the restoration. The abundance and residence of hatchery and naturally spawning fish were not distinguished, as called for in the original objectives, nor did the sponsors differentiate results from pre- and post restoration activities. The data given in several graphs were not interpreted adequately (e.g., water quality graphs) and some graphs received no interpretation at all. The narrative of the main proposal has errors in figure numbering, making the document difficult to follow. The sponsors did not adequately present overall conclusions derived from the first three years of work. Based on the results presented by the sponsors, it does not appear that the objectives of the original proposal were achieved satisfactorily. The objectives of the current proposal are improved somewhat over the original proposal, but essential information is still missing. For example, the sponsors appear to be evaluating fish use of restored sites by comparison with reference sites, although they do not say so explicitly. If this is the case, the sponsors should have provided a more complete description of both the restoration and reference sites to demonstrate that the reference sites are similar in physical characteristics to the restored sites prior to initiation of restoration activities. They refer to the reference sites as “undeveloped” but do not describe what “undeveloped” means. Does it mean relatively pristine or disturbed with no restoration actions taken? The sponsors propose to compare fish use of mainstem sites with wetland sites. It is unclear what this comparison will reveal since fish could move regularly between the mainstem and wetlands. The rationale for selection of the trapping and seining sites is not given. The information given on some key elements such as characteristics of the habitat to be restored is sketchy. The broad vegetation types are provided, but important data are lacking. The description of Devils Elbow, one of the areas to be restored, is not put in the context of the main proposal. The sponsors propose to measure prey utilization by fish and prey abundance in the wetland areas, but they do not describe the analytical methods that will be used to link the two. The proposal has no objective for measuring physical changes in the habitat. The sponsors rely on the assumption that, "Restoration of historic habitat diversity will restore life history diversity within populations (salmon will occupy restored estuarine habitats and derive survival benefits from that use)." The sponsors proposed possible life history patterns of salmon in the Chinook River but did not explain these patterns or describe how they were derived. Overall, the objectives and approach do not appear to have been adequately thought through; therefore, it is doubtful whether meaningful results can be obtained from this work.