Petty Mountain Restoration Project
Project ID: 5636
Status: Completed
Fiscal Year: 2022
Submitted By: 177
Project Manager: Bob Christensen
PM Agency: U.S. Forest Service
PM Office: Ashley National Forest
Lead: U.S. Forest Service
WRI Region: Northeastern
Description:
Stream improvement and meadow restoration on Petty Mountain.
Location:
Located on the Petty Mountain area of the Uinta Mountains. Ashley NF, Duchesne County
Project Need
Need For Project:
The Petty Mountain Restoration project has two objectives as follows - 1) improving 806 acres of mountain meadows and riparian willow complexes that have been experiencing conifer encroachment - and 2) improving approximately 0.6 miles of stream channel and the adjacent wetland Long term monitoring indicates a trend of mountain meadow habitat being displaced by encroaching conifer, potentially reducing resources associated with these dry to saturated meadows. The amount of available habitat determines, to a large degree, the abundance of wildlife on National Forest lands. A reduction in fire frequency during the past 50-80 years due to increased fire suppression has permitted many of the plant communities to reach maturity. This has resulted in widespread successional advances in conifer communities, including heavy fuel build-up, loss of associated plants and a reduction in carrying capacity for early successional stage wildlife, while increasing habitat for late successional stage wildlife. Mountain meadows and willow complexes throughout the Uinta Mountains have experienced conifer encroachment, putting at risk a loss of habitat for plants and animals. There is a need to maintain mountain meadow habitat by removing the young, encroaching conifer. By doing so it is anticipated that within the meadow soil moisture will increase, improving forage for wildlife and livestock and maintaining a diverse ecosystem. Habitat improvement is needed not only to maintain forage quality, quantity, and distribution, but also for the maintenance of existing plant and wildlife diversity.
Objectives:
The objectives are twofold - 1) improving 806 acres mountain meadows and riparian willow that have been experiencing conifer encroachment - and 2) improving wetland and riparian function through stream and meadow restoration. Removing encroaching conifers from these mountain meadows and willow complexes will maintain existing plant and wildlife diversity in these communities on Petty Mountain. This will result in maintaining diverse plant populations associated with meadows, increase soil moisture, improve habitat for wildlife, maintain open space for recreation, maintain perennial vegetation for watershed protection and maintain available forage for wildlife and livestock. Another indirect affect to maintaining watershed health includes an increase in water quality and quantity for fish and other aquatic life, such as the Colorado River cutthroat trout that exists within Hells Canyon Creek, which is within treatment units.
Project Location/Timing Justification (Why Here? Why Now?):
Monitoring indicates a trend of mountain meadow and willow complex habitat being displaced by encroaching conifer, potentially displacing resources associated with these dry to saturated areas. This puts at risk a loss of habitat for plants and animals. If left untreated, cost per acre will increase as trees increase in size. This proposed project will reduce the risk of fuel loading and hazardous fuels within and surrounding meadow habitat creating a larger buffer to potentially manage a wildfire or future prescribed fire. This type of project may have helped slow down the nearby East Fork wildfire of 2020. The direct stream improvements are designed to stop and reverse downcutting and desiccation of the stream and adjacent wet meadows. The unknown alteration of hydrologic function after the East Fork fire makes the stream work an urgent need due to the potentially larger sediment loads.
Relation To Management Plan:
Utah Statewide Elk Management Plan 1. The proposed plan addresses concerns discussed in Habitat Section III. 2. Population Objective 2: Identify future habitat restoration projects with stakeholders. 3. Watershed Restoration Initiative Goals a) Increase forage production by annually treating a minimum of 40,000 acres of elk habitat. b) Coordinate with land management agencies, conservation organizations, private landowners, and local leaders through the regional Watershed Restoration Initiative working groups to identify and prioritize elk habitats that are in need of enhancement or restoration. i) Identify habitat projects on summer ranges (aspen communities) to improve calving habitat. ii) Encourage land managers to manage portions of forests in early succession stages through the use controlled burning and logging. Controlled burning should only be used in areas with minimal invasive weed and/or safety concerns. Utah Mule Deer Statewide Management Plan 1. The proposed project falls with in crucial mule deer habitat restoration priority areas. 2. Habitat Objective 2: Improve the quality and quantity of vegetation for mule deer on a minimum of 500,000 acres of crucial range by 2019. 3. Work with land management agencies, conservation organizations, private landowners, and local leaders through the regional Watershed Restoration Initiative working groups to identify and prioritize mule deer habitats that are in need of enhancement or restoration. Forest Plan The proposed action has been reviewed and is conformance with the Forest Land Management Plan FLMP (1986) for the Ashley National Forest. The FLMP identifies the need and gives specific direction and objectives for management and maintenance of critical habitat by means of treating conifer encroachment. Additional FLMP objectives which are included in the Allotment Management Plans for each allotment include: 1. Manage the habitat of all T&E or sensitive plant, fish, and animal species to maintain or enhance status (Objective 3, IV-30). 2. Maintain or improve soil stability, site productivity, and repair or stabilize damaged watersheds (Objective 2, IV-39). 3. Maintain or improve riparian areas and riparian dependent resource values including wildlife, fish, vegetation, watershed, and recreation in a stable or upward trend. Manage for species diversity (Objective 1, IV-45). 4. Manage vegetation to enhance the riparian ecosystem (Objective 2, IV-46). 5. Maintain natural complexity and high relative productivity of riparian areas (IV-45). 6. Riparian areas will be given a high priority for rehabilitation in range improvement, fish and wildlife improvement, watershed restoration, road maintenance, and KV programs (IV-46). 7. Manage vegetation in riparian areas to be in good or excellent ecological condition, with a stable or upward trend (IV-46). Statewide Moose Plan The project meets the following strategies in the Statewide Moose Plan. B. Habitat Management Goal Strategy c. Work with public land management agencies to minimize, and where possible, mitigate loss or degradation of moose habitat.; Strategy e. Initiate prescribed burns, timber harvests, and other vegetative treatment projects to improve moose habitat lost to ecological succession or human impacts.; and f. Under the Utah Watershed Restoration Initiative, design, implement, and monitor the effectiveness of habitat improvement projects to benefit moose and other wildlife. Colorado River Cutthroat Trout Conservation Strategy The project meets the following Objective in the CRCT Conservation Strategy - Range wide Objective 4. Secure and enhance watershed conditions - Strive to improve watershed conditions for CRCT, including development of protocols for monitoring.
Fire / Fuels:
Fire suppression, beetle kill, disease and other factors have created an inappropriate fire regime (frequency and intensity) leaving the Forest and its users vulnerable to large, catastrophic fires. This proposed project will reduce the risk of fuel loading and hazardous fuels within and surrounding meadow habitat creating a larger buffer to potentially manage a wildfire or future prescribed fire. This type of project may have helped slow down the nearby East Fork wildfire of 2020.
Water Quality/Quantity:
The base flows of both creeks should increase as a result of the restoration. After restoration the phreatic zones in the meadows will be significantly larger. The enlarged phreatic (riparian) zones will feed the streams later in the seasons and through periods of drought much better than the current system. The project will also eliminate further downgrading and lowering of water tables which will at least maintain current stream flow levels, which will reduce sediment loads that will improve water quality. Cal State Polytechnic (Fie, 2018) has conducted research on conifer removal and wet meadows. A statistically significant increase in groundwater and soil moistures was documented every year post treatment, and vegetation changed from xeric to mesic indicative of a wet meadow. Similar results would be expected in meadows and willow complexes treated by this project. The proposed project will maintain and/or increase desirable perennial vegetation for watershed protection and reduce soil loss during high flood events and run-off. Streambank protection using cut debris will reduce erosion and increase sediment deposits while increasing water quality. This project occurs is a municipal watershed and may be correlated with the Cow Canyon Spring system which supplies culinary water through Upper Country Water.
Compliance:
The NEPA analysis was completed and a decision signed October 24, 2018. This project complies with all federal and state requirements. This project has all cultural clearances completed. A Joint Stream alteration permit will be required to complete the instream work. The project will comply with the Programmatic General Permit 10 requirements. The information for the permits has been collected and is expected to be permitted before June 30th, 2021.
Methods:
The proposed project includes hand cutting and scattering conifers within designated meadows and willow complexes on Petty Mountain. The project is designed to have minimal disturbance and to target just areas that show encroachment. These areas are typically located at the margins of meadows or scattered young trees throughout. Chainsaws will be used to cut the conifers. This project is part of a larger project (Uinta Mountains Meadow restoration Project) which includes nearly 50 meadows that have been identified for treatment throughout the entire south slope of the Uinta Mountains. The Petty Mountain portion of this project proposes a total of 806 acres to be treated. Encroaching trees/acre range from 1-400 and average approximately 5-15 trees/acre. Size of trees to be treated range from young seedlings to the occasional mature trees. The stream channel (and water table) will be elevated using a series of grade control structures. These structures will vary in size and location. Throughout most of the project area small log structures will be used to control grade and establish pools behind the structures. The small structures will be placed by hand crews. Areas where vertical and near vertical banks exist will be laid back and the fill material placed into the channel along with high quality erosion matting.
Monitoring:
The Ashley National Forest has an extensive monitoring program with thousands of plots and photo points in the project area. These photos and data are repeated on a regular basis. These data will be used to show the effect of the proposed project. Data, including repeat photography, will be collected immediately after treatments at already established sites. These plots will be revisited on a short-term and long-term schedule. A literature search determined a need for more information on meadow restoration. Meadows will be photographed before and after treatment following the Ashley National Forest monitoring program and documented in the 2060 files located at the Supervisors Office. Breeding bird surveys have been conducted in these areas and will continued be conducted to monitor use by bird species. Colorado River Cutthroat Trout (CRCT) are monitored in Hells Canyon Creek and this monitoring will continue every 2-3 years. Stream and meadow restoration will be monitored yearly for the first three years then at three year intervals utilizing both photo points and a modified Multiple Indicator Monitoring (MIM) protocol.
Partners:
The following partners have been consulted for planning and coordination purposes. They have added valuable input and will continue to shape the details of the project. There were no opportunity for treatment on adjacent lands, because all treatment areas on Petty Mountain are high on the mountain and surrounded by several miles of Forest Service land. Coordination before and during the NEPA process included Forest Service resource staff, Grazing permittees, Utah Grazing Improvement Program, Utah Division of Wildlife, and Utah State University.
Future Management:
Removing conifer encroachment from mountain meadows and willow complexes on Petty Mountain is prat of the larger Uinta Mountain Meadow restoration project that encompasses a total of 17,000 acres on the south slope of the Uinta Mountains. Several projects are currently being proposed by the Ashley National Forest to manage vegetation resources (aspen, conifer/timber, pinyon/juniper, shrub). Monitoring will dictate re-treatment as needed. Conifer encroachment is also affecting aspen stands adjacent to meadows. The Ashley National Forest is working on an aspen project to treat these areas. The stream restoration area will be monitored to determine if/when reentry is needed. Due to the remote nature of Cow Park and utilization of wooden grade control structures reentry is expected in approximately 30 years.
Sustainable Uses of Natural Resources:
The project occurs within active grazing allotments. Conifers removed from suitable grazing land is expected to increase forage. Removal of trees may help in the movement of livestock and allow for better access from one meadow to another. Material cut may be used for range improvement projects (log fences, wood stays, etc.). Open meadows will improve public experience related to hunting, camping, wildlife viewing, and other general outdoor activities including firewood gathering.
Budget WRI/DWR Other Budget Total In-Kind Grand Total
$57,700.00 $7,000.00 $64,700.00 $8,500.00 $73,200.00
Item Description WRI Other In-Kind Year
Contractual Services Contract to cut encroaching conifers on 806 acres of mountain meadows and willow complexes on Petty mountain. The contract is estimated to be $40,300 at $50/acre. $40,300.00 $7,000.00 $0.00 2022
Contractual Services Conservation Corps Contractual Service for stream and meadow restoration (4 weeks) In-Kind- Planning and Oversight $13,200.00 $0.00 $8,500.00 2022
Materials and Supplies Stream Restoration Items (rebar, cable, erosion mat, and block and tackle) $4,200.00 $0.00 $0.00 2022
Funding WRI/DWR Other Funding Total In-Kind Grand Total
$57,700.00 $7,000.00 $64,700.00 $8,500.00 $73,200.00
Source Phase Description Amount Other In-Kind Year
DNR Watershed U004 $29,901.76 $0.00 $0.00 2023
DNR Watershed U004 $12,798.24 $0.00 $0.00 2022
Rocky Mountain Elk Foundation (RMEF) S025 $5,000.00 $0.00 $0.00 2022
MDF Expo Permit ($1.50) S053 $10,000.00 $0.00 $0.00 2022
United States Forest Service (USFS) $0.00 $7,000.00 $8,500.00 2022
Species
Species "N" Rank HIG/F Rank
Colorado River Cutthroat Trout N2 R1
Threat Impact
Improper Forest Management Low
Colorado River Cutthroat Trout N2 R1
Threat Impact
Inappropriate Fire Frequency and Intensity Very High
Domestic Livestock
Threat Impact
Not Listed NA
Elk R2
Threat Impact
Improper Forest Management High
Elk R2
Threat Impact
Inappropriate Fire Frequency and Intensity High
Moose R3
Threat Impact
Improper Forest Management Low
Moose R3
Threat Impact
Inappropriate Fire Frequency and Intensity Low
Mule Deer R1
Threat Impact
Improper Forest Management High
Mule Deer R1
Threat Impact
Inappropriate Fire Frequency and Intensity High
Mule Deer R1
Threat Impact
Problematic Plant Species – Native Upland High
Habitats
Habitat
Aquatic-Scrub/Shrub
Threat Impact
Channel Downcutting (indirect, unintentional) High
Emergent
Threat Impact
Channel Downcutting (indirect, unintentional) Medium
Emergent
Threat Impact
Inappropriate Fire Frequency and Intensity Low
Mountain Meadow
Threat Impact
Soil Erosion / Loss High
Riverine
Threat Impact
Channel Downcutting (indirect, unintentional) High
Project Comments
Comment 01/12/2021 Type: 1 Commenter: Tory Mathis
I don't think the "plant material development" threat on the mountain meadow habitat really applies. Did you intend to select the "soil erosion/loss" threat instead?
Comment 01/13/2021 Type: 1 Commenter: Bob Christensen
I agree with the suggested change. The stream channel and stream bank work with this project will address the threat of "soil erosion/loss". Changed the threat as suggested. There isn't any explanation in the database as to what "plant material development" is. I originally selected that one, because conifers encroaching into mountain meadows could be viewed as unwanted "plant material" that is "developing" in mountain meadows.
Comment 01/13/2021 Type: 1 Commenter: Tory Mathis
A list of the threats to both species and habitats, with descriptions of what they mean, can be found at https://watershed.utah.gov/wp-content/uploads/2015/08/List-of-Threats-for-Utah-WAP_WRI-with-definitions.pdf. The "plant material development" threat is listed under the broader threats of "inadequate restoration tools" and "crucial data gaps." As I understand it, it means that we don't have good sources of plant materials for restoring that habitat type. A project addressing that threat might be working to develop seed sources or researching seeding/planting methods for species that characterize that habitat.
Comment 01/13/2021 Type: 1 Commenter: Bob Christensen
Ok, that explanation makes sense. Thanks for the information and also for the link you provided for those definitions.
Comment 01/15/2021 Type: 1 Commenter: Jimi Gragg
Yep, Tory nailed it. Thanks Tory!
Comment 01/20/2021 Type: 1 Commenter: Bob Christensen
Yes, I agree. Thanks for the comment Jimi.
Comment 01/12/2021 Type: 1 Commenter: Tory Mathis
Could you explain how this project addresses the threat of "brush eradication/vegetation treatments" for the aquatic scrub/shrub habitat? My initial thought is that it would only be included if you were actively restoring vegetation (e.g. planting willows) that had previously been removed. I don't see any of that in this proposal. But I'm willing to entertain another justification if you have one. Also, I think there are other threats you could include for this habitat. Channel Downcutting (indirect, unintentional), for instance.
Comment 01/13/2021 Type: 1 Commenter: Bob Christensen
I agree with the suggested change. I selected both threats listed for "channel downcutting" for "direct" and "indirect, unintentional". The stream channel and stream bank work with this project will "directly" address the threat of "channel downcutting". The conifer removal part of the project may be an "indirect, unintentional" effect to address the threat of "channel downcutting". Removing conifers from the willow and riparian area around hells canyon creek would allow more vigorous growth of willow and riparian vegetation, thereby contributing to soil retention and bank stabilization along the stream, which would help reduce channel downcutting.
Comment 01/13/2021 Type: 1 Commenter: Tory Mathis
Can I kindly suggest that you are thinking about the threats in the wrong way? It appears that you are looking at the wording in the threats and trying to apply that wording to your project activities. Instead, the wording describes what threat the habitat has been facing. Your job is to identify the threats that your project is addressing. For instance, the "Channelization/Bank Alteration (direct, intentional)" threat to a stream would refer to someone coming into the stream and "cleaning" or straightening the channel to provide for more efficient water delivery--in other words, turning it into a ditch. A project addressing that threat would be trying to undo the intentional effort of someone else. If your stream didn't experience deliberate dredging, rip-rap, etc., then this threat would not apply. I suggest you take some time to review the threat definitions found at https://watershed.utah.gov/wp-content/uploads/2015/08/List-of-Threats-for-Utah-WAP_WRI-with-definitions.pdf. I like the project, I just want to make sure we're accurately accounting for the threats.
Comment 01/13/2021 Type: 1 Commenter: Bob Christensen
ok, that's a good explanation. I deleted the "direct, intentional" threat on channelization/bank alteration. Thanks for pointing that out and directing me to the correct definitions.
Comment 01/15/2021 Type: 1 Commenter: Jimi Gragg
Again, Tory nailed it. Thanks again, Tory!
Comment 01/20/2021 Type: 1 Commenter: Bob Christensen
Agreed
Comment 01/16/2021 Type: 1 Commenter: Jimi Gragg
Bob, I definitely think you should add Riverine to your listed of affected habitats, as you explicitly state your intention to improve stream miles. Also, but only if there's some truly wet meadow in your project area now, or you believe you'll get some wet meadow back once you remove some of those tall skinny water pumps - I would add Aquatic - Emergent. Wet meadow is a type of marsh, and the WAP habitat "Mountain Meadow" is based on a LANDFIRE BPS (Rocky Mountain Subalpine-Montane Mesic Meadow (BpS 11450)) that is drier than - that does not include - true wet meadow. The details are, well, detailed/complicated but it all gets down to the fact that wetland mapping in Utah was incomplete and badly outdated when we were putting the WAP together in 2013-2014. However you are fortunate, in the publication of RMRS-GTR-378 in 2018: Riparian and wetland ecosystems of the Ashley National Forest: An assessment of current conditions in relation to natural range of variation.
Comment 01/20/2021 Type: 1 Commenter: Bob Christensen
Ok, thanks for the comment Jimi. I added both Riverine and Emergent as you suggested. These habitats do fit under the stream improvement part of this project, and yes there is a stream (Hells Canyon Creek) and wet meadows within the lop and scatter portion of the project.
Comment 01/27/2021 Type: 1 Commenter: Bryan Engelbert
I'm very supportive of the project. I have some suggestions notes to add for input: 1. I think the authors did a great job in identifying and describing the terrestrial components but I think the project might gain some points, especially under the "Need for Project" and "Ecological Risks" sections by further describing the project's aquatic and stream habitat components. I'm not seeing why the stream habitat work is needed listed in those sections and what threats are being addressed by the work. Some other sections could use some additional detail on exactly why CRCT would benefit beyond improving water quality (beyond the assumption of reducing fine sediments). 2. Under Objectives tab, it may be an overstatement to say directly that CRCT live in the treatment zone; the furthest upstream I have been able to detect them in the Hells Canyon system is right about Mill Spring (marked on topo maps), about 1/4 mile below the lowest stream treatment polygon. It would be easy to say that the adjacent fish population would benefit from increased stream discharge and less fine sediments. 3. Under the "Relation to Management Plans" tab, there is a redundant entry for CRCT strategies. I would delete the listing that is currently posted above the Elk Management plan since the accepted plan is not just DWR's. The lower posting doesn't have this. 4. I believe the stream work described in the project would require a 404 permit which should probably be discussed under the Compliance tab, whether a permit will be needed or has already been filed. 5. Not sure what the pre or post project monitoring for fish population was/is planned; I have survey records from 2007 and 2016 that could be helpful.
Comment 01/29/2021 Type: 1 Commenter: Bob Christensen
Good catch on duplication of CRCT in the "Relation to Management Plans" section. The first reference to CRCT is deleted as suggested. Couldn't find mill spring on the topo. If Mill spring is in Mill park, then it is within the lop and scatter units and CRCT will be indirectly benefitted.
Comment 01/29/2021 Type: 1 Commenter: Bryan Engelbert
It's right at the bottom of the park. I would state that I believe your interpretation is correct and CRCT will be benefitted through those mechanisms.
Comment 02/01/2021 Type: 1 Commenter: Bryan Engelbert
Hey guys, one quick additional comment to try and score more points. I knew the fire burned kind of close to the project area but didn't realize there was burn area within the catchment until Ryan noted that today at the meeting. I think it would help to discuss this (at least from the aquatic health standpoint) in the Need for project, Objectives, and water quality categories briefly. Ryan, you noted that some of the planned instream structure would help mitigate or alleviate some of the post-fire issues (completely agreed); but I don't see that type of fire rehab potential mentioned in the current project wording. With a fire in the drainage, there will undoubtedly be nuisance sediment issues to the downstream cutthroat trout population and any potential to mitigate that problem is great.
Comment 08/23/2023 Type: 2 Commenter: Alison Whittaker
This is just a reminder that completion reports are due August 31st. Expenses have been entered in the Through WRI/DWR column on the finance page. Please do not make any changes to numbers in the Through WRI/DWR column. Any "Through Other" or "In-kind" expenses will need to be entered by the PM or contributors. Be sure to click on the finalize button on the completion report when you have your completion report ready to be reviewed by WRI Admin. Don't forget to upload any pictures of the project you have of before, during and after completion. Thanks.
Comment 08/28/2023 Type: 2 Commenter: Alison Whittaker
Thanks Bob - Will you please update your map features to show what was actually completed? Please also enter any missing expenses, highlighted in rust, on the Finance Page. When you have completed that please go back to the Completion Form and finalize your report again so I know that it has been completed. Thanks.
Comment 08/29/2023 Type: 2 Commenter: Bob Christensen
ok, the map features are updated and I also updated FS expenses.
Comment 08/30/2023 Type: 2 Commenter: Alison Whittaker
Thanks for making those additions. I have moved this project to completed.
Completion
Start Date:
07/12/2021
End Date:
07/22/2021
FY Implemented:
2022
Final Methods:
The lop and scatter portion of the project was completed by a hand crew using chainsaws. The stream restoration portion of the project will not be completed.
Project Narrative:
The purpose of the project was to restore the mountain meadows and stream stability in the Petty Mountain area. Encroaching conifers were removed from mountain meadows to maintain the meadow community for the benefit of wildlife species such as elk, deer, moose and other mountain meadow obligate species. Originally, 806 acres were proposed for lop and scatter, but it was found that the East Fork Fire had burned some of the area. Therefore, the completed acres were reduced to 696 acres. This part of the project was completed to project specifications. The Stream restoration of the project was delayed pending water right permitting. In 2023 it became evident that the Forest Service would not get the permit to do the stream restoration. Thus the stream restoration portion of the project will not be completed.
Future Management:
Repeat photography will be conducted to monitor the lop and scatter portion of the project as well as migratory bird surveys. It is anticipated that treatment would not be needed again for 30+ years.
Map Features
ID Feature Category Action Treatement/Type
12989 Terrestrial Treatment Area Vegetation removal / hand crew Lop and scatter
Project Map
Project Map