FY07-09 proposal 199401806
Jump to Reviews and Recommendations
Section 1. Administrative
Proposal title | Tucannon Stream and Riparian Protection, Enhancement, and Restoration |
Proposal ID | 199401806 |
Organization | Columbia Conservation District |
Short description | Implement habitat protection, enhancement, and recovery strategies to support Subbasin Plan identified ESA focal, cultural significant and species of interest recovery within the Tucannon Subbasin. |
Information transfer | Results provided via BPA Metric reporting, Annual Report Of Accomplishments submitted to BPA and project monitoring and evaluation reports. |
Proposal contact person or principal investigator |
Contacts
Contact | Organization | |
---|---|---|
Form submitter | ||
Debra Nordheim | Columbia Conservation District | [email protected] |
All assigned contacts | ||
Terry Bruegman | Columbia Conservation District | [email protected] |
Debra Nordheim | Columbia Conservation District | [email protected] |
Section 2. Locations
Province / subbasin: Columbia Plateau / Tucannon
Latitude | Longitude | Waterbody | Description |
---|---|---|---|
46* 26' 25 | 117* 44' 56 | Tucannon River | Tucannon River (65.87 miles with lat & lon at Marengo) incompassing Subreaches: Mountain Tucannon (MTN, 10.28 miles from rm 46.26 to 56.54); Hatchery-Little Tucannon (HL, 7.85 miles from rm 38.41 to 46.26); Tumalum-Hatchery (TH, 4.06 miles from rm 34.35 to 38.41); Marengo-Tumalum (MT, 8.37 miles from rm 25.98 to 34.35); Pataha-Marengo (PM, 14.02 miles from rm 11.96 to 25.98) ;Lower Tucannon & it's tributaries(LT, 21.87 miles from 0.0 to 11.96 plus 9.33 miles of tributaries) |
Section 3. Focal species
primary: Chinook Snake River Fall ESUprimary: Chinook Snake River Spring/Summer ESU
primary: Steelhead Snake River ESU
secondary: Bull Trout
Section 4. Past accomplishments
Year | Accomplishments |
---|---|
2005 | 3 off-site water systems. 17.7 ac CREP. 4 screen/flow meters. 0 trees due to drought. 600 ac of School Fire reseeded. 1.0cfs & 180.0ac ft water trusted. Temp. Modeling & Cobble Embeddedness studies. |
2004 | 32,691 trees. 1 off-site water system. 2604 ft riparian fence. 22 screen/flow meters. 2.598cfs & 264.88acft water trusted. Subbasin Management Plan. Milestone Assess. |
2003 | 28,360 trees planted. 197.5 ac in CREP. 420.5 ac conservation tillage. 18,228.4 ft riparian fence. 2 off-site water systems. 8 screen/flow meters. 6.4cfs & 243acft water trusted. Model Plan Milestone Assess. Subbasin Management Plan. |
2002 | 127,705 trees planted. 414.6 ac in CREP. 650.2 ac conservation tillage. Monitor habitat projects & water temp.(WDFW). Lead & particpated in WCC Limiting Factors, HB-2415 Plan, DOE IFIM & TMDL, 2496 SRFB Lead, & begain Snake River Salmon Recovery processes |
2001 | 5 instream habitat projects(6 lg & 44 sm-med pools, 1175 ft LWD & complexity) 77,370 trees. 1332.1 ac conservation tillage. 154.6 ac in CREP. Monitor habitat projects(WDFW). Water quality monitoring(WSU).Subbasin Summary. |
2000 | 11 instream habitat projects(18 lg & 72 sm-med pools, 4490 ft LWD & complexity, 1 off-channel rearing) 69,276 trees, 1852 ac conservation tillage. Monitor habitat projects(WDFW). Water quality monitoring(WSU). 168.5 ac in CREP. |
1999 | 9 instream habitat projects(22 lg & 89 sm-med pools,6146 ft LWD & complexity, 1 off-channel rearing) 26,000 trees. 1870.6 ac conservation tillage. 2 upland sediment basins. Monitor habitat projects(WDFW), ISCO-sediment samplers & water quality(WSU). |
1998 | 12 instream habitat projects (15 lg & 146 sm-med pools, 5540 ft LWD & complexity, 1 off-channel rearing, 1 irrgation mod). 11,891 ft riparian fence. 10,000 trees. 2665.24 ac conservation tillage. WDFW monitor instream project performance. |
1997 | Final Model Watershed Plan. Provide WDFW equip. to monitor water temp. 12 instream projects (8 lg. & 98 sm-med pools, 6828 ft LWD & complexity, 3 off-channel rearing, 1 irrigation mod). 5762 ft riparian fence. 7000 trees. 663.7 ac conservation tillage. |
1996 | 20 instream habitat project creating 5 lg & 125 sm-med pools, 4620 ft LWD & complexity, 1 off-channel rearing, 1 irrigation mod. 3100 ft riparian fence. 500 trees planted. Repaired 1 riparian desilting basin. Built 1 upland desilting basin. |
1995 | Conducted an on-the-ground reach-by-reach habitat condition assessment. Completed 1st draft of the Model Watershed Plan. |
1994 | Installed a series of 3 desilting basins in spring chinook spawning and rearing reach as a wetland enhancement and sediment control project. |
1993 | Initiated Model Watershed Plan. IFIM study. 4,700 ft riparian fencing. 2 limited access & 1 off-river water sites. Created pools via instream habitat structures. Planted 1,460 native trees. |
1992 | Wrote 14 PL-566 conservation plans incompassing 13,823.5 ac. Planted 3,043 native trees and shrubs in riparian areas using volunteer fishermen. |
1991 | Received Congressional funding for the Tucannon PL-566 program. |
1990 | Created additional pool with debris, via boulder clusters and christmas trees, and planted 1900 native trees within the 2.5 mile demonstration site. |
1989 | Created 28 lg. & med. resting pools via habitat structures & planted 7200 native trees along a 2.5 mile length of river as a demonstration site. |
1988 | Wrote 11 Conservation Farm Plans encompassing 2927.1 ac of farm ground in the drainages of the 2 sediment basins. |
1987 | 2 lg. sediment basins installed with combined drainage of 5336 ac. in prime spring chinook spawning area. Basins caught 3971 tons of sediment the first year. 8000 ft. riparian fencing. 10,049 trees planted (willows, alder, cottonwood, vine maple, pine) |
1986 | Conducted a riparian tree density study in collaboration with WDFW. |
1985 | Finalized USDA PL-566 process for submittal. |
1984 | Initiated USDA PL-566 process for watershed assessment and funding for implementation of BMP's for agriculture, range, & riparian areas. |
Section 5. Relationships to other projects
Funding source | Related ID | Related title | Relationship |
---|---|---|---|
BPA | 199401807 | Habitat For Fall Chinook, Stee | This encompasses the Pataha Creek, a major tributary to the lower Tucannon. It negatively effects habitat and water quality in the lower Tucannon where fall chinook spawn, steelhead rear, and bull trout over winter. |
BPA | 200001900 | Tucannon River Spring Chinook | Supplementation to increase natural production in the Tucannon |
Other: WCC | 06-46-IE-01 | Irrigation Efficiencies | Provides cost share funding for irrigation system updates if sufficent water is saved and trusted as an instream flow allocation via the Washington Water Trust. |
Other: USDA/WCC | 06-46-CR-01 | Conservation Reserve Enhancement Program (CREP) | Provides 10% of installation and 100% of maintenance, years 1 through 5, to establish Riparian Forest Buffers and associated BMP's. |
PCSRF - WSRFB | 02-1544 | Tucannon River Screens Phase 2 | Provides cost share funding to install NMFS, USFWS, and WDFW compliant fish screens for irrigation withdrawals. |
PCSRF - WSRFB | 01-1226 | WDFW Wm T Wooten Riparian Proj | Provide cost share funding to install CREP riparian buffer BMP's on WDFW lands along the upper Tucannon. Installation to be completed by 2008. |
Other: WDOE | C0300164 | Flow Meters | Provide cost share funding to install flow meters on irrigation withdrawals. |
BPA | 200001900 | Tucannon River Spring Chinook | Provides supplementation to the Tucannon River. |
Other: LSRCP | none | Lyons Ferry Hatchery Monitoring and Evaluation | Evaluation of hatchery supplementation in the Snake River Region - mitigation of empacts due to hydrosystem. |
Section 6. Biological objectives
Biological objectives | Full description | Associated subbasin plan | Strategy |
---|---|---|---|
HL 1.1-2 or more piece of LWD per channel width. | Reach or exceed two pieces of LWD/channel width. Increase in LWD densities will increase survival of steelhead (fry, subyearling rearing, overwintering and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 4, 5, 6, 12, 13, & 14 for Objective PM 2.1 |
HL 2.1-Increase pools to 10% or more of stream. | Increase the proportion of primary pools to 10% or greater of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (fry, subyearling rearing, overwintering and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 10, & 11 for Objective PM 3.1 |
HL 3.1-Exceed 75% riparian function | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to exceed 75% riparian function. Increase in riparian function and a decrease in confinement will increase survival of steelhead (fry, subyearling rearing, overwintering and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 7, 14, & 15 for Objective PM 4.1 |
MT 1.1-2 or 2+ pieces of LWD/channel width | Reach or exceed two pieces of LWD/channel width. Increase in LWD densities will increase suvival of steelhead (fry, subyearling rearing, overwintering, and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 4, 5, 6, 12, 13, & 14 for Objective PM 2.1 |
MT 2.1-Increase pools to 10-15% of stream area. | Increase the portion of primary pools to 10-15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase suvival of steelhead (fry, subyearling rearing, overwintering, and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 10, & 11 for Objective PM 3.1 |
MT 3.1-Initiate riparian recovery to 60% function. | Initiate riparian recovery and re-estblishment in heavily degraded areas to achieve 60% riparian function. Increase in riparian function and a decrease in confinement will increase survival of steelhead (fry, subyearling rearing, overwintering, and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 7, 14, & 15 for Objective PM 4.1 |
MT 4.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (fry, subyearling rearing, overwintering, and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 7, 10, 11, 23, & 24 for Objective PM 5.1 |
MTN 1.1-1 piece LWD/channel width below Panjab | Increase LWD to more than one piece/channel width below Panjab Creek. Increase in LWD densities will increase survival of steelhead (fry, subyearling rearing, overwintering, and yearly rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, spawning, subadult rearing, juvenile rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 4, 5, 6, 12, 13, & 14 for Objective PM 2.1 |
MTN 1.2-Increase LWD through natural recovery | Increase LWD to achieve a naturally function system through natural recovery and recruitment above Panjap Creek. Increase in LWD densities will increase survival of steelhead (fry, subyearling rearing, overwintering, and yearly rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, spawning, subadult rearing, juvenile rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 4, 5, 6, 12, 13, & 14 for Objective PM 2.1 |
MTN 2.1-Increase pools to 15% or more below Panjab | Increase the proportion of primary pools to 15% or greater of stream surface area below Panjab Creek. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (fry, subyearling rearing, overwintering and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 10, & 11 for Objective PM 3.1 |
MTN 2.2-Increase pools above Panjab | Increase the proportion of primary pools to achieve a naturally functioning system through natural recruitment of LWD above Panjab Creek. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (fry, subyearling rearing, overwintering and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 10, & 11 for Objective PM 3.1 |
PM 1.1-Reduce embeddedness within the area to 20%. | Reduce embeddedness within the area to 20%. This will also stimulate a corresponding decrease in percent fines and turbidity. Reduction in sediment (turbidity, percent fines and embeddedness) will increase survival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 1.1.18-Install properly designed instream structures, including boulders, vortex rock weirs, for short-term pool formation. |
PM 1.1-Reduce embeddedness within the area to 20%. | Reduce embeddedness within the area to 20%. This will also stimulate a corresponding decrease in percent fines and turbidity. Reduction in sediment (turbidity, percent fines and embeddedness) will increase survival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 1.1.1-Improve the extent, structure, & function of riparian buffers through vegetation planting, managed grazing, selective livestock fencing, and similar practices, including tributaries that contribute to priority areas. |
PM 1.1-Reduce embeddedness within the area to 20%. | Reduce embeddedness within the area to 20%. This will also stimulate a corresponding decrease in percent fines and turbidity. Reduction in sediment (turbidity, percent fines and embeddedness) will increase survival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 1.1.19-Increase landowner participation in federal, state, tribal, and local programs that enhance wtershed condtions(e.g. CRP, CREP, Wetlands Reserve, EQIP, Landowner Incentive, Partners for Fish & Wildlife, Conservation Security, etc.) |
PM 1.1-Reduce embeddedness within the area to 20%. | Reduce embeddedness within the area to 20%. This will also stimulate a corresponding decrease in percent fines and turbidity. Reduction in sediment (turbidity, percent fines and embeddedness) will increase survival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 1.1.20-Seek additional funding sources consistent with current CRP and CREP guidelines to increase individual landowner enrollment in programs that achieve similar goals. |
PM 1.1-Reduce embeddedness within the area to 20%. | Reduce embeddedness within the area to 20%. This will also stimulate a corresponding decrease in percent fines and turbidity. Reduction in sediment (turbidity, percent fines and embeddedness) will increase survival of steelhead(incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 1.1.21-Seek funding sources to develop programs consistant with the goals of CRP & CREP in those areas where such programs are not available (e.g. smaller tibutaries high in the subbasin). |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM2.1.1-Improve the extent, structure, & function of riparian buffers through vegetation plantings, managed grazing, selective livestock fencing, and similar practices, including tributaries that contribute to priority areas. |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 2.1.2-Increase the density of woody vegetation in riparian buffers for long-term recruitment of LWD. |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM2.1.12-Increase landowner participation in federal, state, tribal, and local programs that enhance wtershed condtions(e.g. CRP, CREP, Wetlands Reserve, EQIP, Landowner Incentive, Partners for Fish & Wildlife, Conservation Security, etc.) |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 2.1.13-Seek additional funding sources consistent with current CRP and CREP guidelines to increase individual landowner enrollment in programs that achieve similar goals. |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 2.1.14-Seek funding sources to develop programs consistant with the goals of CRP & CREP in those areas where such programs are not available (e.g. smaller tibutaries high in the subbasin). |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 2.1.3- Add LWD in the form of rootwads, log jams, and similar structures that mimic natural formations. |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 2.1.4- Retain existing LWD and limit removal of newly-recruited LWD. |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 2.1.5- Improve stream sinuosity (e.g. meander reconstruction) to slow stream velocities and facilitate retention of LWD. |
PM 2.1-1 or more piece of LWD per channel width. | Reach or exceed one piece of LWD per channel width. Increase in LWD densities will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 2.1.6- Install properly designed instream structures; including boulders, vortex rock weirs, and LWD for short-term pool formation. |
PM 3.1-Increase pools to 15% of stream area. | Increase the proportion of primary pools to 15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing), spring chinook (fry, subyearling, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 3.1.3- Add LWD in the form of rootwads, log jams, and similar structures that mimic natural formations. |
PM 3.1-Increase pools to 15% of stream area. | Increase the proportion of primary pools to 15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing), spring chinook (fry, subyearling, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 3.1.5- Improve stream sinuosity (e.g. meander reconstruction) to facilitate long-term natural pool formation. |
PM 3.1-Increase pools to 15% of stream area. | Increase the proportion of primary pools to 15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing), spring chinook (fry, subyearling, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 3.1.6- Install properly designed instream structures; including boulders, vortex rock weirs, and LWD for short-term pool formation. |
PM 3.1-Increase pools to 15% of stream area. | Increase the proportion of primary pools to 15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing), spring chinook (fry, subyearling, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 3.1.1-Improve the extent, structure, & function of riparian buffers through vegetation planting, managed grazing, selective livestock fencing, and similar practices, including tributaries that contribute to priority areas. |
PM 3.1-Increase pools to 15% of stream area. | Increase the proportion of primary pools to 15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing), spring chinook (fry, subyearling, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 3.1.2-Increase the density of woody vegetation in riparian buffers for long-term recruitment of LWD. |
PM 3.1-Increase pools to 15% of stream area. | Increase the proportion of primary pools to 15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing), spring chinook (fry, subyearling, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 3.1.10-Increase landowner participation in federal, state, tribal, and local programs that enhance wtershed condtions(e.g. CRP, CREP, Wetlands Reserve, EQIP, Landowner Incentive, Partners for Fish & Wildlife, Conservation Security, etc.) |
PM 3.1-Increase pools to 15% of stream area. | Increase the proportion of primary pools to 15% of stream surface area. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (egg incubation, fry, subyearling rearing, and yearling rearing), spring chinook (fry, subyearling, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 3.1.11-Seek additional funding sources consistent with current CRP and CREP guidelines to increase individual landowner enrollment in programs that achieve similar goals. |
PM 4.1-Continue riparian recovery to 75% function. | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function. Increase in riaprian function and a decrease in confinement will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 4.1.1-Improve the extent, structure, & function of riparian buffers through vegetation planting, managed grazing, selective livestock fencing, and similar practices, including tributaries that contribute to priority areas. |
PM 4.1-Continue riparian recovery to 75% function. | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function. Increase in riaprian function and a decrease in confinement will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 4.1.2-Increase the density of woody vegetation in riparian buffers for long-term recruitment of LWD. |
PM 4.1-Continue riparian recovery to 75% function. | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function. Increase in riaprian function and a decrease in confinement will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 4.1.3-Protect high quality riparian habitats in areas of high development pressure through conservation easements, long-term leases, land exchanges, public ed., promotion of BMPs, alternative grazing strategies & install of alternative livestock water. |
PM 4.1-Continue riparian recovery to 75% function. | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function. Increase in riaprian function and a decrease in confinement will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 4.1.5-Protect riparian vegetation through promotion of livestock BMPs such as alternative grazing rotations & the installation of alternative forms of water for livestock. |
PM 4.1-Continue riparian recovery to 75% function. | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function. Increase in riaprian function and a decrease in confinement will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 4.1.14-Increase landowner participation in federal, state, tribal, and local programs that enhance wtershed condtions(e.g. CRP, CREP, Wetlands Reserve, EQIP, Landowner Incentive, Partners for Fish & Wildlife, Conservation Security programs, etc.) |
PM 4.1-Continue riparian recovery to 75% function. | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function. Increase in riaprian function and a decrease in confinement will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 4.1.7-Protect wetland and riparian habitats through land conservation easements, long-term leases, land exchanges, public ed., & promotion of urban, forestry, & agricultural BMPs, where applicable. |
PM 4.1-Continue riparian recovery to 75% function. | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function. Increase in riaprian function and a decrease in confinement will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 4.1.15- Seek additional funding sources consistent with current CRP and CREP guidelines to increase individual landowner enrollment in programs that achieve similar goals. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.1-Improve the extent, structure, & function of riparian buffers through vegetation planting, managed grazing, selective livestock fencing, and similar practices, including tributaries that contribute to priority areas. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.2- Increase the density of woody vegetation in riparian buffers for long-term recruitment of LWD. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM5.1.3- Protect high quality riparian habitats in areas of high development pressure through conservation easements, long-term leases, land exchanges, public ed., promotion of BMPs, alternative grazing strategies & install of alternative livestock water. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.5- Protect riparian vegetation through promotion of livestock BMPs such as alternative grazing rotations & the installation of alternative forms of water for livestock. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.6- Conduct appropriate shade resotration activities where streamside shading has been reduced by anthropogenic activities. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.7- Protect wetland and riparian habitats through land conservation easements, long-term leases, land exchanges, public ed., & promotion of urban, forestry, & agricultural BMPs, where applicable. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.23- Increase landowner participation in federal, state, tribal, and local programs that enhance wtershed condtions(e.g. CRP, CREP, Wetlands Reserve, EQIP, Landowner Incentive, Partners for Fish & Wildlife, Conservation Security, etc.) |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.24- Seek additional funding sources consistent with current CRP and CREP guidelines to increase individual landowner enrollment in programs that achieve similar goals. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.10- Decrease the width-to-depth ratio through instream improvements, selective bank stabilization & other methods. The use of "hard" stabilization methods such as rip rap, concrete, or railroad ties is discouraged. |
PM 5.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (incubation, fry, subyearling rearing, and yearling rearing life history stages), spring chinook (fry, subyearling rearing, overwintering, and pre-spawning life history stages) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | PM 5.1.11- Improve stream sinuosity (e.g. meander reconstruction) to facilitate long-term natural pool formation. |
TH 1.1-1+ pieces LWD/channel width below Cummings | Maintain more than one piece of LWD/channel width below Cummings Creek. Increase in LWD densities will increase survival of steelhead (fry, subyearling rearing, overwintering, and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 4, 5, 6, 12, 13, & 14 for Objective PM 2.1 |
TH 1.2-2 pieces LWD/channel width above Cummings | Increase LWD to two pieces/channel width above Cummings Creek. Increase in LWD densities will increase survival of steelhead (fry, subyearling rearing, overwintering, and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning) and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 4, 5, 6, 12, 13, & 14 for Objective PM 2.1 |
TH 2.1-Increase pools to 10% of stream area | Increase the proportion of primary pools to 10% of stream surface area below Cumming Creek. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (fry, subyearling rearing, overwintering and pre-spawning), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 10, & 11 for Objective PM 3.1 |
TH 2.2-Increase pools to 15% of stream area | Increase the proportion of primary pools to 15% of stream surface area above Cumming Creek. Increase in primary pool quantity, quality and complexity will increase survival of steelhead (fry, subyearling rearing, overwintering and pre-spawning), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 10, & 11 for Objective PM 3.1 |
TH 3.1-Achieve 40-50% riparian function | Continue riparian recovery (increasing riparian complexity, width, and re-estblishment) to achieve 40-50% riparian function below Cummings Creek. Increase in riparian function and a decrease in confinement will increase survival of steelhead (fry, subyearling rearing, overwintering and pre-spawning), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 7, 14, & 15 for Objective PM 4.1 |
TH 3.2-Achieve 75% riparian function | Continue riparian recovery (increasing riparian complexity, width, and re-establishment) to achieve at least 75% riparian function and increased riparian complexity from Cummings Creek to the Hatchery. Increase in riparian function and a decrease in confinement will increase survival of steelhead (fry, subyearling rearing, overwintering and pre-spawning), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 7, 14, & 15 for Objective PM 4.1 |
TH 4.1-Decrease summer daily water temperatures. | Decrease summer daily maximum temperatures to no more than 4 days greater than 75*F (24*C) and show progress toward meeting Washington State temperature standards and TMDL goals. Decrease in summer temperatures will increase suvival of steelhead (fry, subyearling rearing, overwintering and yearling rearing), spring chinook (fry, subyearling rearing, overwintering and pre-spawning), and bull trout (adult migration, juvenile outmigration, subadult rearing life history stages). | Tucannon | See Strategies 1, 2, 3, 5, 6, 7, 10, 11, 23, & 24 for Objective PM 5.1 |
Section 7. Work elements (coming back to this)
Work element name | Work element title | Description | Start date | End date | Est budget |
---|---|---|---|---|---|
Produce Environmental Compliance Documentation | Project Environmental Compliance | Develop Cultural Resource Surveys, NEPA checklists, and Biological Assessments as required for identified projects. | 10/1/2006 | 9/30/2010 | $32,000 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics |
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Increase Instream Habitat Complexity | Increase key instream habitat complexity quantity and quality. | Increase key instream habitat diversity and complexity to move toward biolgical objective levels. | 10/1/2006 | 9/30/2010 | $320,000 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 4.1-Decrease summer daily water temperatures. |
Metrics * # of stream miles treated: 1.5 * # of structures installed: 36 |
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Lease Land | CREP 5 year Extension | Extend CREP contracts for an additional 5 year period by providing landowner/contract holder with an up-front payment. Riparian recovery and longevity are critical for restoration success. | 10/1/2006 | 9/30/2010 | $400,000 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics * # of riparian miles protected: 28.9 * # of acres of new lease: 602.9 |
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Coordination | Coordinate activities to implement the Tucannon Subbasin plan. | Participate in coordination of regional planning processes; subbasin, Snake River Salmon Recovery, WRIA 35 Watershed planning, regional project monitoring plan . Coordinate the development of projects to implement the Tucannon Subbasin Plan. | 10/1/2006 | 9/30/2010 | $57,625 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics |
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Identify and Select Projects | Develop and/or update potential project lists | Project files developed, in conjunction with technical agency personnel, for each project to include initial scoping and design. Serve as a clearing house for project selection. | 10/1/2006 | 9/30/2010 | $22,687 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics |
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Manage and Administer Projects | Tucannon Subbasin Plan Project Implementation | Project management and administrative work related to implementation of the Tucannon Subbasin Plan projects. | 10/1/2006 | 9/30/2010 | $150,698 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics |
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Outreach and Education | Community Involvement in Habitat Restoration | Activities that involve local and agency personnel in habitat protection, enhancement, and restoration. | 10/1/2006 | 9/30/2010 | $3,000 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics * # of general public reached: 75 * # of students reached: 60 * # of teachers reached: 5 |
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Produce Annual Report | Annual Report | Annual report describing all project accomplishments for each fiscal year. | 10/1/2006 | 9/30/2010 | $3,700 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics |
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Produce Pisces Status Report | Milestone Status | Report progress toward reaching milestones | 10/1/2006 | 9/30/2010 | $2,500 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics |
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Collect/Generate/Validate Field and Lab Data | Habitat project site attribute evaluation. | Contract with WDFW to measure and evaluate pre-installation and post-installation project site habitat attibutes and to continue cooperative effort to monitor water temperature throughout the basin. | 10/1/2006 | 9/30/2010 | $38,000 |
Biological objectives HL 1.1-2 or more piece of LWD per channel width. HL 2.1-Increase pools to 10% or more of stream. HL 3.1-Exceed 75% riparian function MT 1.1-2 or 2+ pieces of LWD/channel width MT 2.1-Increase pools to 10-15% of stream area. MT 3.1-Initiate riparian recovery to 60% function. MT 4.1-Decrease summer daily water temperatures. MTN 1.1-1 piece LWD/channel width below Panjab MTN 1.2-Increase LWD through natural recovery MTN 2.1-Increase pools to 15% or more below Panjab MTN 2.2-Increase pools above Panjab PM 1.1-Reduce embeddedness within the area to 20%. PM 2.1-1 or more piece of LWD per channel width. PM 3.1-Increase pools to 15% of stream area. PM 4.1-Continue riparian recovery to 75% function. PM 5.1-Decrease summer daily water temperatures. TH 1.1-1+ pieces LWD/channel width below Cummings TH 1.2-2 pieces LWD/channel width above Cummings TH 2.1-Increase pools to 10% of stream area TH 2.2-Increase pools to 15% of stream area TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function TH 4.1-Decrease summer daily water temperatures. |
Metrics |
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Collect/Generate/Validate Field and Lab Data | Sediment & Cobble Embeddedness Sampling | Contract with USFS to operate ISCO sediment samplers and perform cobble embeddednes sampling to measure impacts thoughout the subbasin. | 10/1/2006 | 9/30/2010 | $15,000 |
Biological objectives HL 3.1-Exceed 75% riparian function MT 3.1-Initiate riparian recovery to 60% function. PM 1.1-Reduce embeddedness within the area to 20%. PM 4.1-Continue riparian recovery to 75% function. TH 3.1-Achieve 40-50% riparian function TH 3.2-Achieve 75% riparian function |
Metrics |
Section 8. Budgets
Itemized estimated budget
Item | Note | FY07 | FY08 | FY09 |
---|---|---|---|---|
Personnel | 1.1 FTE split between Lead, Assistant, & Engineer (utilizing composite rates which include benefits) | $68,764 | $70,827 | $72,952 |
Travel | mileage | $2,002 | $2,070 | $2,138 |
Supplies | Office and operations | $6,942 | $7,150 | $7,365 |
Other | Contract Services/Cost-share - Land Lease | $120,000 | $130,000 | $150,000 |
Other | Contract Services/Cost-sahre - Instream Habitat | $95,072 | $111,881 | $113,047 |
Other | Contracted Services - Environmental/Cultural Resources | $18,000 | $7,000 | $7,000 |
Other | Contracted Services - M & E | $20,000 | $20,000 | $13,000 |
Totals | $330,780 | $348,928 | $365,502 |
Total estimated FY 2007-2009 budgets
Total itemized budget: | $1,045,210 |
Total work element budget: | $1,045,210 |
Cost sharing
Funding source/org | Item or service provided | FY 07 est value ($) | FY 08 est value ($) | FY 09 est value ($) | Cash or in-kind? | Status |
---|---|---|---|---|---|---|
WSRFB | cost share | $92,000 | $100,000 | $130,000 | Cash | Under Development |
Totals | $92,000 | $100,000 | $130,000 |
Section 9. Project future
FY 2010 estimated budget: $382,727 FY 2011 estimated budget: $382,727 |
Comments: Budget suggests a 5% annual increase. |
Future O&M costs: Project O&M is the responsibility of the landowner unless a catastrophic natural event occurs. In the case of a natural event, impacts on per-project bases will be evaluated for possible cost share assistance to maintain project intent.
Termination date: 2021
Comments: Tucannon Subbasin Plan implementation anticipated a 15 year schedule. Continuous annual funding will allow implementation of strategies on a progressive base for accumulative gains in meeting biological objectives.
Final deliverables: Reports documenting habitat gains impacting focus species life-cycle survivability and Tucannon ecosystem function. Reports will be from monitoring and evaluation efforts contracted to resource agencies, BPA BiOp Metrics, and project Pisces and annual accomplishments.
Section 10. Narrative and other documents
199401806 FY2007 ISRP Response | 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] | ||||||
$331,333 | $331,333 | $331,333 | $993,999 | Expense | ProvinceExpense | Fund |
NPCC DRAFT FUNDING RECOMMENDATIONS (Sep 15, 2006) [full Council recs] | ||||||
$331,333 | $331,333 | $331,333 | $0 | ProvinceExpense | ||
Comments: ISRP fundable qualified: programmatic habitat m&e issue, see decision memo discussion. |
ISRP PRELIMINARY REVIEW (Jun 2, 2006)
Recommendation: Response requested
NPCC comments: This work has been ongoing for a sufficient amount of time to have made significant progress from the past reviews, but it includes no description of biological benefits nor does it demonstrate adaptive management. The history of the project is more reassuring than the proposed work. It puts more emphasis on riparian types of work. Perhaps the instream part of this project could be terminated. Sponsors did provide some information to show impact of projects on physical structure of the channel, but none to show the biological benefits. The data (Tables 1 and 2) presented are difficult to interpret. Many more pools were reported in 2000 than in 1998, but the stream got wider and shallower. Stream discharge was greater in 2000 than in 1998 making it difficult to assign the observed differences to project activities. Data in Table 12 are offered as evidence of benefits for fish, but these data need to be compared to similar data from both control and treatment sites before the alterations were made if it is to have any meaning. Demonstrated value of the work depends on availability of information to describe changes that have occurred as a result of the project and whether or not these changes are consistent with the project objectives. Even if the impact of project actions on fish and other aquatic organisms is ignored, sponsors need to answer questions concerning impacts on substrate composition, bank stability, stream temperature, and the hydrograph. Site specific actions taken to alter the physical structure of a stream and to overcome a perceived problem often result in unintended consequences making it important to initiate actions only with a clear understanding of dynamics in the entire system. Actions at one site are only reasonable when taken with a complete understanding of their potential impact at other locations. The ISRP is concerned that the focus of the project appears to have changed to development of bio-engineered instream structures. The project needs to return to its original purpose. That is "... increasing pool and spawning habitat quality and quantity through geomorphic stabilization, riparian bio-function restoration, increasing complexity, maintaining adequate flow, and reducing water temperature and sediment." The project needs to ensure reviewers that competent and experienced fluvial-geomorphologists have assisted in design, evaluation, and choice of projects that will provide a high probability for gaining geomorphic stability, and that sufficient change is possible to attain subbasin objectives for the system. These inputs should be in place before new actions are taken. NMFS comments from the province review are consistent with the ISRP's view that bioengineering projects should be limited to "fine-tuning" once watershed function has been restored. The ISRP requests responses to at least the following items. 1. What information is available to help assess whether or not the work that has been completed under this project has made any progress in reaching its objectives? 2. Can observed changes in the channel be attributed to project activities or did similar changes occur in other channels? 3. What assistance has been incorporated in the project from competent and experienced fluvial-geomorphologists? 4. What is the geomorphic basis for the projects that have been completed and proposed projects? 5. What is the basis for and the estimated probability that completed and proposed projects will attain desired channel conditions given the limitations imposed by alternative uses of the water and floodplain?
ISRP FINAL REVIEW (Aug 31, 2006)
Recommendation: Fundable (Qualified)
NPCC comments: Questions and comments from the ISRP were clarified for a number of issues as best as possible. Some data is reported on fish density, but it is not clear that the project personnel are adaptively managing based on these data. It's not clear that the structures are actually benefiting the fish. They likely need another year to see if anything is changing. Project sponsors provided some sediment/embeddedness measures from sampling by the U.S. Forest Service in 2005. These data can at least provide a baseline for assessments in the future, both in the mainstem and to help assess activities in the Pataha Creek basin. They also provided a 2002 progress report that provided some baseline data for temperature and for fish densities at several index sites, data that might be useful in the future. Statistical analysis of fish density data from control and treatment sites showed no significant differences between sites. Temperature data did not provide a basis for describing any trends in the system. Qualification: Since there are no data and thus no scientific justification for continuing this project, it would have to be continued based on a qualification that the substrate, temperature, and fish density work be continued in such a way that decisions are possible regarding the effectiveness of project activities. The sponsors should make full use of data from other fish monitoring projects in the basin to help meet this requirement.