Purpose of Analysis: This is intended to be a conceptual screening analysis to be used for evaluating the proposed alternative to determine if it warrants additional analysis or consideration.
Alternative
Description:
Fund (Licensee funding level
not yet determined) the implementation of
coldwater watershed improvement via projects as well as appropriate aquatic
resources and water temperature monitoringquality studies
throughout the upper North Fork Feather River (NFFR) watershed, including the
East Branch (EB) and other tributaries. The Plumas County Flood Control and Water Conservation District
(PCFC&WCD) in cooperation with Feather River Coordinated Resource
Management (FR-CRM) currently has an ongoing watershed
improvement program.
For
this alternative, tThe Plumas County Flood Control and
Water Conservation District (PCFC&WCD) willwould
implement selected
projects in cooperation with Feather River Coordinated Resource
Management (FR-CRM) and other groups (e.g. Plumas Water Forum, Resource
Conservation Districts). The projects
will be designed to address stream temperature improvement to support the
protection ofand additional beneficial uses as
described in the Central Valley Regional Water Quality Control Board Basin Plan
including cold freshwater habitat, domestic and agricultural water supply,
recreation, and wildlife habitatand hydropower
generation. The activities initiated under this alternative will
include ongoing prioritization for both public (including National Forest Service
lands) and private lands and may include those identified as priority projects
to address on-going temperature and sediment issues in the NFFRorth Fork
Feather River in existing studies and planning documents such as
FR-CRM MOU (1985) and Feather River Watershed Management Strategy (2004). The activities will be consistent with
guidance included within the Integrated Regional Water Management Plan (Plumas
County, July 2005).
Depending upon the funding
levels, pPotential projects identified at this
time for possible
implementation in the first fifteen years of the license are
included on the attached list, and include water temperature effectiveness
monitoring as necessary to determine the project’s
effectivenessthroughout the term of the license. During the implementation phase, water temperature
monitoring of existing and constructed projects will provide a
feedback loop to maximize the effectiveness of projects as they are
implemented. Depending upon the funding
levels, tThis alternative maywill
include the following actions:
· Implement priority restoration projects as identified in existing plans for the watershed or identified in the future by the implementing authority. Foster and support innovative restoration projects.
·
Develop
a water
temperature monitoring plan that addresses project effectiveness
and contributes to increased understanding of stream water temperature
dynamics and coldwater sources during late summer months. The water
temperature monitoring plan will also track the sustainability of
implemented projects and identify any maintenance needs. Consider utilizing thermal imaging
technology (helicopter flights currently used) to establish baseline stream
temperatures, identify cold and warm water sources and provide periodic review
of benefits derived. Continuous recording thermographs maywill
be installed at key areas throughout the watershed to build on the existing
FR-CRM network. The monitoring plan will include an aquatic
resources and habitat monitoring component on a sub-watershed scale to
complement other monitoring efforts in the watershed.
· Maintain or modify implemented projects if necessary to establish project self-sustainability.
·
Develop a central data archive as a repository to collect water
temperature monitoring information that is currently maintained by
various entities and to utilize information more efficiently, track activities,
and monitor results. This information
will assist in determining real and potential effects in the EB and the NFFR,
and the downstream effects of restoration projects on water temperature and aquatic
productivity in the watershed.
· Utilize information from selected stream restoration projects to aid in future project design considerations.
·
Identify and implement as appropriate on-site
and off-site projects that reduce temperature, reduce sedimentation,
and improve aquatic habitat. This may include culvert modification, fish ladder
installation, and other measures to improve access to cold-water refugia.
Assumptions:
·
This alternative assumes that all reasonable
on-site alternatives to reduce daily mean water temperatures to 20 degrees C in
the NFFR within the FERC 2105, 1962, and 2107 project boundaries have been
identified. Actions (except for construction of the Prattville
Curtain) included in the FERC 1962 license to address temperature have been
implemented. Comment:
this last sentence is very confusing so I suggest eliminating it.
·
Modeled and measured daily mean water temperature
will exceed the 20 degrees C goal in the NFFR within the project boundaries
even with implementation of any of the previously evaluated 24 water
temperature controlreduction
alternatives either singularly or in combinationpreviously
evaluated.
· Portions of the NFFR and EB watersheds can be restored to improve cold-water habitat.
· It is possible to bring alluvial valley and canyon streams in Plumas County much closer to their natural function to provide cold-water habitat and cold-water supply.
· The Union Pacific Railroad, CalTrans, and other landowners will be invited to become active participants in the watershed restoration activities, especially regarding fish passage into coldwater tributary channels in the NFFR Canyon. Landowners that benefit from the watershed improvements will be expected to contribute funding as appropriate.
· It is unknown what synergistic effect upper watershed restoration activities would have on temperatures within the lower Belden, Rock Creek-Cresta and Poe reaches. Long-term monitoring of these actions may show a reduction of EB thermal input to the NFFR system. On-going project monitoring in the watershed has shown local water temperature improvements resulting from restoration (see Attachment 1 showing monitoring results from 1985-2005)
· Funding will be escalated for inflation through the term of the license.
· Plumas County Flood Control and Water Conservation District (PCFC&WCD) will implement projects in cooperation with Feather River Coordinated Resource Management (FR-CRM) and will continue to seek leveraged funding from other sources.
Rationale:
· Water-temperature modeling efforts have shown the EB to be a primary source of warmer water into North Fork project waters between the confluence with the NFFR and Belden Powerhouse.
· Available information (Integrated Regional Water Management Plan, July 2005) prioritizes the following specific sub-watersheds within the NFFR watershed as suitable and cost-effective for restoration: Last Chance; Red Clover; Spanish Creek; Lower Indian; Upper Indian; Lake Davis-Long Valley; and Sierra Valley. (See Attachment 2).
· Potential for leveraging other funding sources (See Attachment 3) will assist in providing adequate total long-term funding for a watershed restoration and improvement program.
·
Headwater
areas can more readily be fully restored to proper fluvial and floodplain
function (less land use restrictions).
Restoration can result in reduced peak run-off and extend the natural
hydrograph to help reduce downstream water temperature in the EBast Branch
and extendincrease
natural base flows.
· Opportunities to work in mid-watershed valleys to maintain headwater water temperature and other beneficial uses (e.g. Indian, American, Genesee valleys) will require the interest of willing landowners. While landowner interest has been slowly but steadily evolving, the pace is expected to increase markedly above existing levels due to new (2004) Clean Water Act Agricultural Waiver compliance regulations.
· The EB includes priority sub-watersheds associated with large floodplains and valleys as identified in the Feather River Watershed Management Strategy (Monterey Agreement, 1994).
· Biological connectivity – Rehabilitation of the upstream watershed has the potential to help seed lower river reaches with excess productivity from increased macroinvertebrate, fishery, and riparian communities.
· Other water quality improvement benefits from watershed restoration and improvements include reduced sedimentation and turbidity.
Other Considerations:
·Potential for salmonid fish
passage actions that might necessitate additional enforcement personnel to
address poaching (relates to measurement criteria to be used to evaluate
effectiveness of upstream restoration activities) Comment:
this does not make sense here;
it is a CDF&G law enforcement issue, not a
watershed restoration and improvement issue.
· Supports implementation of Central Valley RWQCB Agricultural Waiver Compliance Program
Implementation Strategy:
The alternative would have a ‘front-loaded’ schedule to initiate selected restoration activities during the first 15 years after issuance of a new project license (FERC No. 2105) and allow adequate time to monitor long-term synergistic responses within the NFFR watershed and provide valuable information for use during future NFFR relicensings.
Conclusions:
The potential benefits of the NFFR Watershed
Restoration and Improvement Alternative are
significant and include but are not limited to improving stream health, water
quality and other beneficial uses in both upper watershed and possiblelower
project waters. The NFFR Watershed Restoration and Improvement Alternative
also includes compiling water temperature monitoring information
from selected
programmultiple agencies’ stream restoration
projects and the potential to leverage outside funding for expanded project
implementation and management. To be fully successful, this alternative
requires a long-term commitment of resources from multiple
parties, from which the Licensee’s portion of resourceswhich
wouldill
be guaranteed through FERC enforcement of license articles. The Proposed alternative warrants
additional analysis and consideration.
Attachment 1:
Projects Completed and Benefits Monitored 1985-2005*
Stream Name/Phase Project Type |
Total Treated Miles/Acres |
Total Cost/ Completion Date |
Fishery Benefits1 |
Temperature Benefits2 |
Other Benefits Observed |
Comments |
Last Chance Valley Cottonwood/Big Flat Meadow re-watering |
1.0/47 |
$100,000
1995 |
Pre-restoration: no trout observed Post-restoration: 1,280 trout per mile |
Estimated 2˚C water temp decrease in treated area in 1998 |
Downstream spring flow duration extended. Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion |
|
Last Chance Valley- Clarks Creek Phase I Meadow Re-watering |
1.0/56 |
$75,000
2001 |
No data available |
No data available |
Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion |
Project implemented during drought |
Last Chance Creek- Stone Dairy Meadow re-watering |
0.6/22 |
$56,000
2001 |
No defined channel for fish habitat |
No data available |
Decreased erosion; increased water storage. Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
Intermittent drainage |
Last Chance Creek Mainstem Phase I (CalFed) Meadow re-watering |
7.0/800 |
$980,000
2004 |
Fish population in Last Chance Creek watershed steady decline in three sampling efforts between 1997-2005; unknown causal factors. No post-restoration data available |
Measured 10.7ºF water temp decrease for 4.8 miles in June 2004; 1.7ºF water temp decrease in daily maximum at Jordan Flat June-July 2005; 4.5ºC water temp decrease at Alkali Flat. |
Decreased erosion; increased water storage. Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
Water temperature monitoring difficult due to ephemeral channels. Last Chance Ck. is still recovering from project construction completed in 2004. Additional restoration to continue in 2005. |
Red Clover Creek Demonstration Project Check dams |
1.0/70 |
$172,000
1985 |
Pre-restoration: no trout observed Post-restoration: 4-32 trout observed in pools behind check dams |
No data available |
Waterfowl habitat improved; 588 waterfowl in project acre; 23 waterfowl in control area |
Lack of spawning habitat is a limiting factor. Accurate sampling in ponds problematic. Coldwater refugia created by deep ponds behind check dams and immediately downstream |
Red Clover Creek- Bagley Creek Meadow re-watering |
0.3/15 |
$9,000
1997 |
No data available |
No data available |
Decreased erosion; increased water storage. Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
|
Indian Creek- Boulder Creek Meadow re-watering |
0.6/30 |
$22,000
1997 |
No data available |
No data available |
Decreased erosion; increased water storage. Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
|
Indian Creek -Ward Creek Meadow re-watering |
1.0/165 |
$220,000 1999 |
No data available |
No data available |
Decreased erosion; increased water storage. Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. Increased waterfowl and deer populations. |
|
Indian Creek- Hosselkus Creek, Phase I /II Meadow re-watering |
0.75/65
|
$156,000
2001/2006 |
Not applicable |
Measured 4.5˚C water temperature decrease thru 1400’ of treated area on June 27, 2005 |
Increased water storage; Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
Ephemeral stream channel – no fish habitat |
Indian Creek - Wolf Creek Phases I-III (through the town of Greenville) Geomorphic channel reconstruction and re-vegetation |
2.5/70 |
$600,000
1990-1999 |
Pre-restoration: no trout captured Post-restoration: no trout captured in 2001 or 2003 |
Pre-restoration: No data available Post-restoration: daily water temp increase <1ºF in one mile of treated area through Greenville |
Terrestrial and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
Lack of trout capture may be result of urban setting. A temperature increase of less than 1˚F is a significant improvement where vegetation response has been very slow |
Spanish Creek - Greenhorn Creek (Farnworth property) Geomorphic channel reconstruction and re-vegetation |
0.75/20 |
$150,000
1991 |
Pre-restoration: 2 trout captured in 408’ of project area.
|
No data available |
Decreased erosion; increased in recreational fishery; Terrestrial and riparian vegetation and wildlife habitat improved; |
|
*Data provided on this table are from various monitoring files housed by FR-CRM, PG&E, DWR, DFG and antidotal observations. The accuracy of the data provided on this table has not been verified at this time.
1 Fishery benefits are based on results of electro-fishing, and are highly variable due to other variables such as flow, precipitation, and air temperatures.
2 Monitoring efforts on these projects were largely limited to one year pre-project and one year post-construction measurements to confirm conformance to construction specifications. Long-term, consistent monitoring will be necessary to measure water temperature improvements in meadow re-watering projects. Water temperature improvements appear to be expressed when additional groundwater stored as a result of the project begins to augment the surface water, downstream of the actual project work. Detecting change may require more sampling points both within and downstream of the project area to capture water temperature changes.
Attachment 2:
Priority 1 Project Reaches: Estimated Costs1 and Anticipated Benefits2
Stream Name/Phase Project Type |
Total Area to be Treated – Miles/Acres |
Estimated Costs/ Completion Date |
Anticipated Fishery Benefits |
Anticipated Water Temperature Benefits |
Other Benefits Anticipated |
Comments |
Last Chance Creek/Mainstem Phase II Meadow Re-watering |
9.0/800 |
$2,800,000
2007 thru 2009 |
Trout fishery expected to increase, with most benefits taking up to 5 years |
Maximum daily temperatures expected to decrease by up to 10ºF at Doyle Crossing |
Increased water storage; Terrestrial, aquatic, and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
Improvement in temperature will be due to increased off channel water storage and delayed summertime release |
Last Chance Creek/Clarks Creek Phase II Meadow Re-watering |
1.0/70 |
$100,000
2009 |
No change in fishery is expected |
Decrease of 1-2ºF at confluence of Clarks and Last Chance creeks; |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
Improvement in temperature will be due to increased off channel water storage and delayed summertime release |
Last Chance Creek/Mainstem Phase III Meadow Re-watering |
10.0/1000 |
$3,000,000
2009 thru 2011 |
Increased trout fishery |
Decrease of daily maximum water temps. By up to 5ºF |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity. |
This area not as impaired as Mainstem Phase II, so smaller temp. benefits anticipated |
Red Clover Creek/Phase I Meadow Re-watering |
3.5/375 |
1,100,000
2005 thru 2006 |
Pre-restoration: one trout observed in 2004; 9 trout observed in 2005 Anticipate increased trout fishery; aquatic ecosystem improvement
|
Pre-restoration: daily maximum water temp increase of 6.3ºF measured in treated area from 6/15-8/31, 2005 Post-restoration: No data available Anticipate decreased water temperatures in same area |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
Project construction planned to begin in 2006 |
Red Clover Creek/Phase II Meadow Re-watering |
2.0/200 |
$400,000
2008 thru 2010 |
Anticipate increased trout fishery |
Decrease of 1-3ºF through project reach. |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
|
Red Clover Creek/Dixie Creek Phase I Meadow Re-watering |
1.0/90 |
$75,000
2005 thru 2007 |
Improve aquatic habitat, including trout. |
Little or no change |
Increased water storage; Decreased erosion. Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity |
Relatively small project; primary goal is to stop headcut moving upstream |
Red Clover Creek/Dixie Creek Phase II Meadow Re-watering |
5.0/150 |
$750,000
2011 thru 2013 |
Unknown fishery; general aquatic habitat should improve |
Expected to decrease due to increased riparian vegetation |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
Limited benefits expected due to small size of watershed |
Red Clover Creek/Dixie Creek Phase III Meadow Re-watering |
7.0/1000 |
$1,050,000
No construction date identified |
Expect cumulative fishery benefits from all three phases |
Decrease in maximum daily temp. of 10-15ºF at Notson Bridge from all three phases of project |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
|
Indian Creek/Genesee Valley Geomorphic channel and revegetation |
6.0/200 |
$2,400,000
2006 thru 2012 |
Expect improved trout biomass of 30% above Flournoy Bridge from 2003 levels (2,350 ml/100 yds) and 100% at Taylorsville (365 ml/100 yds) |
Up to a 10ºF decrease in maximum daily temperatures from all Last Chance and Red Clover projects through Genesee Valley |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
|
Indian Creek/Indian Valley Geomorphic channel and revegetation |
7.0/170 |
$2,800,000
2008 thru 2015 |
Anticipate increased trout fishery |
Maintenance of the 10-15ºF decrease accomplished by upstream restoration projects |
Increased water storage; Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
|
TOTALS |
50/3780 |
$13,525,000 |
|
|
|
|
1 All costs are estimates in today’s dollars. Costs reflect only survey, design, permitting and construction expenses.
2 Anticipated benefits are based on professional judgment and past experience of Plumas County representativeswith similar projects.
Priority 2 Project Reaches: Estimated Costs1 and Anticipated Benefits2
Stream Name/Phase Project Type |
Total Area to be Treated – Miles/Acres |
Estimated Costs/ Completion Date |
Anticipated Fishery Benefits |
Anticipated Water Temperature Benefits |
Other Benefits Anticipated |
Comments |
Spanish Creek – American Valley Geomorphic channel and revegetation |
7.0/170 |
$2,800,000
2007 thru 2009
|
Expect to improve trout fishery by 30% above 2003 level (115 ml/100 yds) |
Decrease maximum daily temp by up to 5ºF after vegetation becomes established (5 years) |
Decrease sedimentation; increased terrestrial, riparian wildlife habitat |
Trout improvement difficult to establish; fishing pressure an issue at this site; Benefits will be limited to near-channel area |
Spanish Creek – Meadow Valley Geomorphic channel and revegetation |
7.0/170 |
$2,800,000
2006-2010 |
No change predicted |
Limited or no change (1-2ºF decrease) |
Decrease sedimentation; increased terrestrial, riparian wildlife habitat |
Presence of foothill yellow-legged frogs may limit restoration at this site. Benefits will be limited to near-channel area |
Spanish Creek – Greenhorn-Chandler Geomorphic channel and revegetation |
5.0/150 |
$1,250,000
2011 thru 2014 |
Anticipate increased trout fishery |
Decrease in maximum daily temp of 3-8ºF from historic temps of 76 and 77ºF (2003 and 2001, respectively) |
Decrease sedimentation; increased terrestrial, riparian wildlife habitat |
Benefits will be limited to near-channel area |
Indian Creek/Lights Creek, Indian Valley Geomorphic channel or meadow re-watering |
5.0/1000 |
$1,500,000
No construction date identified |
Anticipate increased trout fishery |
Decrease in daily maximum temp of 10-15ºF from historic temps of 84-86ºF (2000-2003) |
Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
Project may be required to comply with RWQCB standards. |
Indian Creek/Cooks Creek, Indian Valley Geomorphic channel or meadow re-watering |
4.0/400 |
$1,000,000
No construction date identified |
Anticipate increased trout fishery |
Unknown |
Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
Project may be required to comply with RWQCB standards.
|
Indian Creek/Wolf Creek, Indian Valley Geomorphic channel and revegetation |
3.0/90 |
$1,250,000
No construction date identified |
Anticipate increased trout fishery however, expect fisheries to be limited by Greenville urban runoff |
Predict maintenance of upstream temp or slight increase (<1ºF) through this reach |
Terrestrial, aquatic and riparian vegetation and wildlife habitat improved; increased riparian and meadow productivity; decreased erosion. |
Benefits will be limited to near-channel area |
TOTALS |
31/1980 |
$10,600,000 |
|
|
|
|
Attachment 3: Historical Funding of Previous Watershed Restoration Projects in Plumas County
Funding Source |
Funded 1990-05 |
% Of Total Funding |
Federal Agencies |
|
|
USDA-United States Forest Service |
$467,650 |
7% |
USDA-Natural Resources Conservation Service |
$82,500 |
1% |
Environmental Protection Agency |
$15,000 |
<1% |
Bureau of Reclamation |
$980,000 |
14% |
|
|
|
State Agencies |
|
|
California Department of Forestry & Fire Protection |
$105,000 |
2% |
State Water Resources Control Board |
$3,422,104 |
49% |
California Department of Water Resources |
$920,500 |
13% |
Central Valley Regional Water Quality Control Board |
$109,000 |
2% |
California Department of Fish & Game |
$100,000 |
1% |
California Department of Transportation |
$100,000 |
1% |
California Department of Parks and Recreation |
$39,930 |
<1% |
UC Cooperative Extension |
$2,100 |
<1% |
|
|
|
County & Local Public Agencies |
|
|
Plumas County |
$234,263 |
3% |
Plumas County Community Development Commission |
$1,900 |
<1% |
Quincy Community Services District |
$3,800 |
<1% |
Plumas Unified School District |
$1,600 |
<1% |
Feather River College |
$1,600 |
<1% |
NorCal Nevada Resource Conservation and Development |
$9,500 |
<1% |
|
|
|
Private Groups |
|
|
Pacific Gas & Electric |
$352,000 |
5% |
Landowners |
$7,710 |
<1% |
Sierra Pacific |
$15,000 |
<1% |
Collins Pine |
$10,000 |
<1% |
Total |
$6,981,157 |
98% |