BPA Fish and Wildlife FY 1997 Proposal
Section 1. Administrative
Section 2. Narrative
Section 3. Budget
see CBFWA and BPA funding recommendations
Section 1. Administrative
Title of project
Wide Hollow Creek Rearing Enhancement Project
BPA project number 5511800
Business name of agency, institution or organization requesting funding
Yakama Indian Nation
Sponsor type WA-Tribe
Proposal contact person or principal investigator
Name | Lynn Hatcher | |
Mailing address | P.O. Box 151
Toppenish, WA 98948 | |
Phone | 509/865-6262 |
BPA technical contact ,
Biological opinion ID
NWPPC Program number
Short description
Wide Hollow Creek historically supported a robust run of spawning coho salmon, as well as steelhead. It is likely that high numbers of spring chinook juveniles also reared in lower Wide Hollow Creek. Today, this channel is in extremely poor condition due to floodplain encroachment, routing of untreated storm water into the channel, irrigation, diking and channelization. Summer rearing in this channel is nil due to high temperatures. Sediment and other pollutants levels are also high. Wide Hollow Creek does not meet water quality standards for DDT, 4,4�-DDE, 4,4'-DDD, Dieldrin, Alpha-Endosulfan, Temperature, Dissolved Oxygen and Fecal Coliform.
This project would address water quality and habitat problems through the following practices:
1. Install juvenile fish passage at the drop structure;
2. design and implement a storm water management plan for the drainage;
3. enhance rearing habitat by restoring riparian vegetation, relieving floodplain constrictions where possible, adding large woody debris and angular rock to the channel; and,
4. implement a public education and involvement program to involve landowners, school districts and interest groups in water quality monitoring, restoration and maintenance.
Project start year 1997 End year 2000
Start of operation and/or maintenance
Project development phase Implementation
Section 2. Narrative
Related projects
Project history
Biological results achieved
Annual reports and technical papers
Management implications
Specific measureable objectives
Fish density will be determined and water quality data will be collected pre- and post-project implementation throughout season of use. Changes in riparian canopy closure will also be measured.
Testable hypothesis
Restoring riparian habitat, improving water quality and adding stream complexity will increase rearing productivity.
Underlying assumptions or critical constraints
The hydrograph will be similar to historic; water quality will remain adequate to support anadromous fish during season of use (i.e. discharge of toxic substances to the stream will not occur); a minimum of twenty percent of the landowners in the project area will participate
Methods
Fish density will be determined by mark and recapture methods. Three reaches will be sampled at three different times during the season of use (early fall through late spring). Equipment will include normal fish sampling tools.
Water quality will be monitored for the following parameters: D.O., temp., BOD, fecal coliform, phosphates and lead.
Changes in riparian canopy will be determined with a densiometer.
Brief schedule of activities
The project would be initiated with the mailing of fliers to landowners. Affected public agencies would also be contacted. Public meetings would be held to discuss stream functions, appropriate management and the goals of the project. Past habitat restoration/protection successes that the Yakama Indian Nation has undertaken would be displayed. Landowners would be solicited to voluntarily initiate riparian restoration/protection on their land. In-channel structures, such as large woody debris, would be placed at appropriate locations. Flood easements at critical locations would be purchased. Engineering studies would be completed to determine the best approach to address stormwater problems. A stormwater management plan would be written and the end of year one. In year two, further riparian restoration projects would be implemented. The action items identified in the stormwater plan would be implemented. Monitoring would occur in years three and four. Ultimately, field trips would be scheduled to display individual restoration projects.
Biological need
Managers believe rearing habitat for juvenile fish is severely limited in the Yakima Basin. This project would redress rearing habitat function through increasing riparian canopy closure, improving stormwater treatment and increasing in-channel habitat complexity.
Critical uncertainties
Rearing habitat for juvenile fish is severely limited in the Yakima Basin, so much so that fish managers believe rearing habitat restoration is one of most important actions to restore stock health.
Summary of expected outcome
Stormwater treatment will improve. Flood impacts would decrease. Native riparian vegetation density will increase. In turn, water quality will improve, in-channel habitat complexity will increase and stream banks will become more stable. Landowners will become more aware of anadromous fish needs and other reasons for effectively treating stormwater and preserving/restoring riparian vegetation. Ultimately, the project will be used as a local demonstration area to encourage additional landowners to protect and restore streams.
Dependencies/opportunities for cooperation
The stormwater plan would have oversite by affected public agencies. Individual restoration projects will be developed in consultation with the USDA - NRCS and the WDOE. Cost-share applications will be presented to the USDA - CFSA, the WDNR, the USFWS, and other agencies that administer funding programs. Hydraulics Permit Applications (HPA�s) will be required for all in-channel work requiring heavy equipment. These will be processed two months prior to anticipated work.
Risks
Invasive weedy species may out-compete native plantings. Flooding may remove large woody debris.
Monitoring activity
Monitoring of water quality revegetation success will be done for three years. Weed control and replanting will be done as necessary.
Section 3. Budget
Data shown are the total of expense and capital obligations by fiscal year. Obligations for any given year may not equal actual expenditures or accruals within the year, due to carryover, pre-funding, capitalization and difference between operating year and BPA fiscal year.Historic costs | FY 1996 budget data* | Current and future funding needs |
(none) | New project - no FY96 data available | 1997: 952,000 1998: 1,008,000 1999: 10,080 2000: 10,080 |
* For most projects, Authorized is the amount recommended by CBFWA and the Council. Planned is amount currently allocated. Contracted is the amount obligated to date of printout.
Funding recommendations
CBFWA funding review group Bonneville Dam - Priest Rapids Dam
Recommendation Tier 2 - fund when funds available
Recommended funding level $952,000