Southern Region Riparian Restoration FY 17
Project ID: 3672
Status: Completed
Fiscal Year: 2017
Submitted By: 318
Project Manager: Heather Talley
PM Agency: Utah Division of Wildlife Resources
PM Office: Salt Lake Office
Lead: Utah Division of Wildlife Resources
WRI Region: Southern
Description:
The dams created by beavers create or improve riparian communities in several ways. This project's objective is to relocate beavers from nuisance situations to watersheds within focus areas that historically supported beaver colonies; thereby, restoring water table levels, floodplain connectivity and improving riparian vegetation.
Location:
Drainages, rivers, and/or streams throughout the Southern Region that may benefit from the removal of, or translocation of beaver. Upper Kanab Creek, Swapp Canyon, Robinson Canyon, Seiler Creek, Mill Creek, Shingle Creek, Moosman, Cottonwood Creek, and Deep Creek.
Project Need
Need For Project:
Beavers have been removed from many drainages and watersheds where they have historically occurred. Beavers contribute important benefits to watersheds such as recharging and raising ground water tables, improving riparian vegetation, expanding wetlands, slowing flood waters, reducing erosion, improving water quality, providing habitat for aquatic species and other wildlife, and providing more biodiversity to the landscape. Landowners, USFS employees, BLM employees, and local communities have expressed interest and support in relocating nuisance beavers and restoring beaver populations in historic, suitable habitat (as explicated in the Statewide Management Plan). Specifically sites identified for translocation in this proposal encompass portions of the headwaters of the East Fork Sevier River on the Paunsaugunt Plateau, streams draining the east side of Mount Dutton and lakes that maintain recreational sport fisheries on Boulder Mountain. The Paunsaugunt Plateau locations are within current and historic habitat for boreal toad, which has seen a dramatic decline in density, distribution and breeding activity over the past 20 years, at least some of which has been attributed to the loss of active and maintained beaver ponds throughout the drainage. WRI project "3631 Paunsaugunt boreal toad habitat improvement project" highlights the need for beaver and beaver habitat to benefit boreal toad populations on the Paunsaugunt. Streams draining the east side of the Mount Dutton were all affected by the 2002 Sanford Fire. Vegetation loss and subsequent flooding led to major erosion and incision on many of these streams. Deep Creek contains a remnant population of Bonneville cutthroat trout, which was extirpated after the fire. Deer Creek and Cottonwood Creek contained nonnative sport fisheries that were extirpated following the fire.Bonneville cutthroat trout (BCT) to have been reintroduced into all three of these streams and are persisting at some level; however, habitat has been slow to recover. Habitat and riparian vegetation have recovered faster where beaver have been able to colonize and maintain themselves (particularly in Deer Creek, see attached images). There is a need to increase habitat complexity and reconnect the floodplain of streams incised following the Sanford fire on Mount Dutton. Re-establishing beavers into approved and suitable watersheds will restore these lost benefits and values, as well as provide an opportunity to diminish or obliterate nuisance issues resulting from beaver damage on private property, without resorting to lethal methods. Some issues associated with nuisance beavers include: impeding flow of irrigation water (blocking pipelines or culverts), flooding property, cutting cottonwoods/aspen/willow. In these circumstances, nuisance beavers would be an excellent source for live trapping and relocating to desirable and suitable locations. If a nuisance area's ecosystem is critically dependent on beaver activity, or is an excellent environment for beavers, flow-control devices may be implemented to sustain beaver activity while resolving the associated nuisance issues.
Objectives:
Improve riparian habitat and biodiversity via re-establishing beavers in approved and suitable watersheds, consequently alleviating nuisance per Statewide Management Plan. Improve boreal toad breeding habitat on the Paunsaugunt Plateau. Improve habitat complexity and help to halt incision and reconnect streams to their floodplain on the east side of Mount Dutton. Improve the holding capacity in Moosman Reservoir and Deer Creek Lake, which should improve the ability of trout to overwinter. Improving habitat for boreal toad, Bonneville cutthroat trout and other riparian and aquatic species will support the WRI arm to enhance Utah's Wildlife and Biological Diversity. Reconnecting the floodplain and raising the water table using beaver supports the WRI arm of Water Quality and Yield for all Uses. To work cohesively with BLM, USFS, NGO's, and any other federal, state, or non-government agency that may be involved with riparian restoration.
Project Location/Timing Justification (Why Here? Why Now?):
Beaver may transport Aquatic Invasive Species (AIS). To eliminate this issue, a 72-hour quarantine period will be required for any beavers from waterways that remain "unknown" in regards to AIS. Beavers from watersheds contaminated with AIS will be held in quarantine for 120 hours. Furthermore, beavers will not be relocated within a four mile radius of a fish hatchery, and those from sources of AIS will not be released in areas designated "critical habitat" for native cutthroat trout. Due to the delicate nature of live trapping, the UDWR has previously attended a workshop with Sherri Tippy to ensure the most meticulous and expedited process is implemented. As highlighted in WRI project 3631 "Paunsaugunt boreal toad habitat improvement project" without continued habitat improvement projects and other conservation actions there is the risk that the Paunsaugunt population of boreal toad may be listed as threatened or endangered which would threaten the WRI arm of "Opportunities for Sustainable Uses" in this area. Additionally, streams on the eastern side of Mount Dutton are slowly recovering from the Sanford Fire the reintroduction of beaver offers a low cost, low risk method of stabilizing those streams and reconnecting their floodplains. Without beaver it could take decades to centuries to regain floodplain connection and habitat complexity unless significantly more costly active stream restoration methods were employed.
Relation To Management Plan:
Utah's Wildlife Action Plan: The goal/purpose of Utah's Wildlife Action Plan is to "To manage native wildlife species and their habitats, sufficient to prevent additional listings under the Endangered Species Act." As discussed above, the Paunsaugunt Plateau population of boreal toad appears to fit the criteria that could lead to it being evaluated as a Distinct Population Segment under the current petition to list an "Eastern population" of boreal toad as threatened or endangered under the Endangered Species Act. Similarly, Bonneville cutthroat trout have been petitioned for listing threatened or endangered under the Endangered Species Act multiple times and translocating beaver to streams on the east side of Mount Dutton would improve their habitat. The WAP has an objective to reduce the scope and severity of channel downcutting for aquatic forested and riverine habitat. It also identifies the following conservation actions to achieve these objectives: 1) Restore aquatic habitat complexity. 2) Restore floodplain connectivity. 3) Increase cover and extent of native riparian vegetation by restoring beaver on the landscape where social and environmental factors permit (per beaver Restoration Assessment Tool). This project will help achieve goals outlined in the Dixie and Fishlake Land and Resource Management Plans by increasing diversity of plant and animal communities (Diversity IV-3), protecting and improving aquatic habitats (Wildlife and Fish, IV-3), improving habitat for sensitive, threatened and endangered species (Wildlife and Fish, IV-4), and maintaining or improving water quality and the productivity of streams and riparian areas (Soil and Water, IV-4). Other multi-agency plans this project will directly benefit include: State of Utah Beaver Management Plan, Range-wide Conservation Agreement and Strategy for Bonneville Cutthroat Trout, Range-wide Conservation Agreement for Southern leatherside chub and the Boreal Toad Conservation Plan in the State of Utah. Examples of specific plan objectives include: UTAH STATEWIDE BEAVER MANAGEMENT PLAN The overall goal of the plan is to "Maintain healthy, functional beaver populations in ecological balance with available habitat, human needs, and associated species." Population Management Objective 1: Maintain reproducing beaver populations within their current distribution in appropriate habitat through 2020. Watershed Restoration Objective 1: Work to improve riparian habitats associated streams and wetlands in a minimum of 10 tributaries through translocating beaver into unoccupied suitable habitat on public and/or private land by 2020. Strategy 9) Encourage land management agencies and private landowners to manage riparian habitat to support translocated beaver populations. Boreal Toad Conservation Plan for the State of Utah: The goal of the Boreal toad Conservation Plan is to "maintain or restore multiple, viable breeding populations in nine of the 14 mountain ranges or geologic areas in Utah where boreal toad historically occurred ." The Plan identifies seven key Conservation Strategies including: "Identify and reduce threats from habitat loss and degradation (Habitat Management). Range-wide Conservation Agreement and Strategy for Bonneville cutthroat trout (Lentsch et al. 2000): Strategy Objective II A) 1) Maintain or restore water quality to a degree that provides for stable and productive riparian and aquatic ecosystems; 2) Maintain or restore stream channel integrity, channel processes, and the sediment regime (including the elements of timing, volume, and character of sediment input and transport) under which the riparian and aquatic ecosystems developed; 5) Maintain or restore the diversity and productivity of desired plant communities in riparian zones; 6) Maintain or restore riparian vegetation to: c) help achieve rates of surface erosion, bank erosion, and channel migration characteristic of those under which the communities developed; Conservation Agreement and Strategy for southern leatherside (Lepidomeda aliciae) in the State of Utah (UDWR 2010): Objective 3 - Identify, prioritize, and implement actions to reduce threats to southern leatherside populations and habitat and evaluate the effectiveness of these actions. Conservation Element B) 2) - Restore habitat where possible, creating habitat complexity and connectivity for southern leatherside. Conservation Element B) 3) - Implement habitat enhancements that may include some or all of the following: removal of diversion structures, modification of barriers to allow fish passage, bank stabilization, enhancement of native vegetation, riparian fencing, nonnative removal and implementation of compatible grazing practices. Conservation Element D) 4) -- Maintain natural hydrologic conditions. This project will also help Forestry Fire and State Lands accomplish objectives, according to the Utah Statewide Forest Resource Assessment and Strategy Guide 2010.
Fire / Fuels:
This project is not directly tied to fire or fuels benefit. However, the benefits of increased riparian vegetation communities may make an area more resilient to wildlife or at the least act as an efficient fire break. Additionally, beavers are taken to areas that have experienced fire damage for landscape rehabilitation.
Water Quality/Quantity:
The very function of beaver dams exemplifies increased water quality and quantity. The creation of ponds decelerates run off and stream flow, curtailing erosion and allowing stabilization of the stream banks. The pooling water additionally raises the water table, consequently creating meadows and riparian vegetation. This also keeps stored water cool underground, releasing water during drought conditions and extending the season of water flow. Finally, filtering out sediment will leave cleaner watersheds downstream, which also benefits multiple species.
Compliance:
UDWR will consult with Federal partners if NEPA is required for installation of flow control devices on a case-by-case basis. Beaver relocations alone will not necessitate any archaeological clearances, and any NEPA is covered by the UDWR Beaver Management Plan. UDWR has juridiction over beaver in Utah as it is considered a furbearer. UDWR also has a statewide Stream Alteration Permit that allows action related to beaver trapping and translocation permissible under state law
Methods:
The UDWR employees will be assessing the impacts of the project through visiting all sites where beaver are transplanted and communicating with other agencies (USFS, BLM, FFSL, etc.), local residents and trappers, as well as other volunteer agencies to ensure beneficial results. The UDWR will monitor the relocation sites that are utilized and address any unforeseen conflicts that may have occurred due to the translocation.
Monitoring:
The UDWR employees will be assessing the impacts of the project through visiting all sites where beaver are transplanted and communicating with other agencies (USFS, BLM, FFSL, etc.), local residents and trappers, as well as other volunteer agencies to ensure beneficial results. The UDWR will monitor the relocation sites that are utilized and address any unforeseen conflicts that may have occurred due to the translocation. Repeat photography will be used to illustrate changes to the landscape due to beaver activity. The request for VHF transmitters will assist in the monitoring process. Though two receivers have been requested so both seasonals will have full access to receivers to monitor when possible, other sections of the DWR and other agencies may also have receivers to be utilized at times. In addition, DWR performs classification flights for big game, and we could capitalize on that opportunity to have biologists on the flights perform some telemetry as well. In addition, the Dixie has Riparian Level II inventory sites along many of the potential translocation sites and can assess changes in greenline vegetation related to reintroductions. UDWR and Forest Service annually monitor boreal toad breeding activity and distribution on the Paunsaugunt. UDWR and Forest Service just completed BCT sampling in the East Fork Sevier River drainage in 2015 and will reassess BCT populations in the drainage by 2022.
Partners:
Forest Service, BLM, NGO's as necessary and Division of Wildlife Resources agree to work together to translocate, monitor, and any other trapping/translocation needs as necessary. In the development of the Beaver Management Plan, advisory committee members included: Utah Trappers Association, Forest Service, Natural Resource Conservation Service, Utah Cattlemen's Association, Utah Farm Bureau, Grand Canyon Trust, BLM, Wildlife Services, DWR. This committee developed this plan including the relocation processes and suitable translocation sites. It was then taken to the RAC and Wildlife Board for approval. Before deciding a relocation site, DWR contacts the pertinent public lands agency, county commissioners, irrigation owners, and any other private property owners that might be affected.
Future Management:
As the Statewide Beaver Management Plan is instated until 2020, the UDWR will continue to apply for funding to transplant beavers every year. Future management in terms of monitoring are explained in the Monitoring section, and any other future management regarding population, AIS, nuisance issues, harvest management, watershed restoration, and/or research is illuminated in the plan. Additionally, the Paunsaugunt is closed to trapping until future recommendations are made. UDWR and the Dixie National Forest are in the process of developing a Conservation Action Plan for the Paunsaugunt Plateau population of boreal toad, which will have a large focus on increasing and maintaining beaver populations on the Plateau. Additionally UDWR and the Forest Service are signatories to the BCT and Southern leatherside chub Conservation Agreements and Strategies. As such both agencies are committed to healthy watersheds, riparian areas and stream habitats where these species occur and encouraging and maintaining beaver support those commitments.
Sustainable Uses of Natural Resources:
Beaver as ecosystem engineers can increase the amount of forage for wild and domestic ungulates. This project is not designed specifically to benefit livestock but may provide secondary benefits by improving the diversity and availability of riparian vegetation. Range conservationists from the USFS adjust stocking rates based on conditions. If conditions of the stream improve, there is no justification for lowering AUMs as the area will have became more resilient and productive.
Budget WRI/DWR Other Budget Total In-Kind Grand Total
$28,330.00 $0.00 $28,330.00 $14,860.00 $43,190.00
Item Description WRI Other In-Kind Year
Personal Services (seasonal employee) Funding towards live-trapping and relocating for one seasonal at 40 hours per week, another seasonal for 20-30 hours per week. Any emergency flow-control device construction and miscellaneous work that needs to be performed. $10,750.00 $0.00 $0.00 2017
Other Travel - seasonals will need to travel far distances and may be required to stay overnight to monitor traps in some instances. $500.00 $0.00 $0.00 2017
Other Vehicle Mileage - seasonals will need to be reimbursed for mileage of their personal vehicle or receive a vehicle from fleet. $9,750.00 $0.00 $0.00 2017
Materials and Supplies Materials and supplies will be purchased if necessary, such as live traps, lure, and materials for flow-control devices or associated needs. $4,000.00 $0.00 $0.00 2017
Other Volunteer work; additional assistance may be acquired by the Forest Service, BLM, and NGO's. Forest Service estimates a value of $8860 of in-kind services; BLM estimates a value of $2000 to be contributed, other NGO's/volunteers; $1,000. $0.00 $0.00 $11,860.00 2017
Materials and Supplies The UDWR will contribute this amount towards materials/supplies that exceed the WRI amount requested. $0.00 $0.00 $3,000.00 2017
Equipment Purchase Tail tag VHF transmitters - $169/transmitter per DWR contract. Requesting 10 transmitters. $1,690.00 $0.00 $0.00 2017
Equipment Purchase Receivers and antennae - r-1000 receiver @ $695/unit. Com Spec antenna @ $125/unit. For two receivers with antennae = $1,640 total. $1,640.00 $0.00 $0.00 2017
Funding WRI/DWR Other Funding Total In-Kind Grand Total
$28,330.00 $0.00 $28,330.00 $14,860.00 $43,190.00
Source Phase Description Amount Other In-Kind Year
Federal Aid (PR) F1659 $3,550.00 $0.00 $0.00 2017
Habitat Council Account HCRF $24,780.00 $0.00 $0.00 2017
United States Forest Service (USFS) $0.00 $0.00 $10,860.00 2017
Utah Division of Wildlife Resources (UDWR) $0.00 $0.00 $3,000.00 2017
Volunteers $0.00 $0.00 $1,000.00 2017
Species
Species "N" Rank HIG/F Rank
American Beaver
Threat Impact
Not Listed NA
Bonneville Cutthroat Trout N4 R1
Threat Impact
Agricultural / Municipal / Industrial Water Usage High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Channel Downcutting (indirect, unintentional) High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Channelization / Bank Alteration (direct, intentional) High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Dam / Reservoir Operation Medium
Bonneville Cutthroat Trout N4 R1
Threat Impact
Droughts High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Hydro Power Facilities Low
Bonneville Cutthroat Trout N4 R1
Threat Impact
Inappropriate Fire Frequency and Intensity Very High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Increasing Stream Temperatures High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Presence of Dams High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Presence of Diversions High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Soil Erosion / Loss Low
Bonneville Cutthroat Trout N4 R1
Threat Impact
Temperature Extremes High
Bonneville Cutthroat Trout N4 R1
Threat Impact
Water Allocation Policies High
Brook Trout R4
Threat Impact
Not Listed NA
Colorado River Cutthroat Trout N2 R1
Threat Impact
Agricultural / Municipal / Industrial Water Usage High
Colorado River Cutthroat Trout N2 R1
Threat Impact
Channel Downcutting (indirect, unintentional) High
Colorado River Cutthroat Trout N2 R1
Threat Impact
Channelization / Bank Alteration (direct, intentional) Low
Colorado River Cutthroat Trout N2 R1
Threat Impact
Dam / Reservoir Operation Low
Colorado River Cutthroat Trout N2 R1
Threat Impact
Droughts High
Colorado River Cutthroat Trout N2 R1
Threat Impact
Hydro Power Facilities Low
Colorado River Cutthroat Trout N2 R1
Threat Impact
Inappropriate Fire Frequency and Intensity Very High
Colorado River Cutthroat Trout N2 R1
Threat Impact
Increasing Stream Temperatures High
Colorado River Cutthroat Trout N2 R1
Threat Impact
Presence of Dams Low
Colorado River Cutthroat Trout N2 R1
Threat Impact
Presence of Diversions High
Colorado River Cutthroat Trout N2 R1
Threat Impact
Temperature Extremes High
Colorado River Cutthroat Trout N2 R1
Threat Impact
Water Allocation Policies High
Elk R2
Threat Impact
No Threat NA
Greater Sage-grouse N3 R1
Threat Impact
Channel Downcutting (indirect, unintentional) Medium
Greater Sage-grouse N3 R1
Threat Impact
Droughts Medium
Mule Deer R1
Threat Impact
Not Listed NA
Waterfowl
Threat Impact
Not Listed NA
Western Toad N4
Threat Impact
Droughts Very High
Western Toad N4
Threat Impact
Improper Grazing – Livestock (current) High
Western Toad N4
Threat Impact
Small Isolated Populations High
Habitats
Habitat
Aquatic-Forested
Threat Impact
Channel Downcutting (indirect, unintentional) High
Aquatic-Forested
Threat Impact
Channelization / Bank Alteration (direct, intentional) High
Aquatic-Forested
Threat Impact
Droughts High
Mountain Meadow
Threat Impact
Soil Erosion / Loss High
Riverine
Threat Impact
Channel Downcutting (indirect, unintentional) High
Riverine
Threat Impact
Channelization / Bank Alteration (direct, intentional) High
Riverine
Threat Impact
Droughts High
Riverine
Threat Impact
Increasing Stream Temperatures Unknown
Riverine
Threat Impact
Sediment Transport Imbalance Medium
Riverine
Threat Impact
Temperature Extremes Unknown
Riverine
Threat Impact
Relationship Between Groundwater and Surface Water NA
Project Comments
Comment 02/10/2016 Type: 1 Commenter: Nicki Frey
Hi Heather, How do you envision this project benefitting greater sage grouse? Thanks, Nicki
Comment 02/26/2016 Type: 1 Commenter: Heather Talley
Hi Nicki! I imagine this project creating areas for brood-rearing habitat via beaver ponds.
Comment 02/19/2016 Type: 1 Commenter: Michael Golden
Hey Heather, A couple of items you may want to consider adding/addressing. 1) There was considerable coordination tin the development of the Beaver Management Plan (e.g. approved by RAC and Wildlife Board, had multiple stakeholder involvement in Plan development and the selection of priority translocation sites) which you do not discuss under the Partners Section. Also I know that you and others are constantly coordinating with the Counties and irrigators prior to any translocation activities. 2)The Dixie had Riparian Level II inventory sites along many of the potential translocation sites and can assess changes in greenline vegetation related to reintroductions. UDWR and FS annually monitoring boreal toad breeding activity and distribution on the Paunsaugunt. UDWR and FS just completed BCT sampling in the East Fork Sevier River drainage in 2015 and will reassess BCT populations in the drainage by 2022.
Comment 02/26/2016 Type: 1 Commenter: Heather Talley
Hey Mike, I appreciate the comments and I have made some changes to the plan. I know I submitted the proposal before finishing the partners section and appreciate the additional input. Thanks!
Comment 02/19/2016 Type: 1 Commenter: Michael Golden
Also may want to mentions that the Paunsuagunt is closed to trapping under future management.
Comment 02/19/2016 Type: 1 Commenter: Keith Day
Heather, Benefits to BAEA are marginal, at best.
Comment 02/26/2016 Type: 1 Commenter: Heather Talley
Keith, thank you for the input, and I have deleted the BAEA from the species list. I want to include the most benefiting species in the proposal.
Comment 02/26/2016 Type: 1 Commenter: Jimi Gragg
Hi Heather, *great* project, thanks a ton for all your work. Just one "negative" comment (not really negative) - I think you should remove any threats to species and habitats, that this project is not directly or indirectly reducing or mitigating. For example, OHV use as a threat to boreal toads - is there going to be any abatement of that threat due to this project? Another example - relationship of ground- & surface water with riverine habitat (that's a data gap) - is there some research or monitoring planned as part of this project to look at that relationship? I'm just looking ahead to when Tyler or Alan or somebody is trying to make the case for program support or performance, and they're generating reports on e.g. all we've done about this threat or that one. It could get awkward for them, is all. Thanks again, I hope you get the OK to put beavers wherever they're wanted and needed.
Comment 02/29/2016 Type: 1 Commenter: Heather Talley
Hi Jimi! Thank you so much for your comments. I did remove the OHV threat - you're right, that the project won't directly address that threat. However, I do think that the beavers provide and increase in surface water and the water table. I found a few different sources that confirmed this claim: "When beaver recolonize stream systems, their impoundments increase base flows, as well as recharge and elevate the water table" (Pollock et al. 2003). "...surface and groundwater storage behind beaver dams high in watersheds may provide a buffer for base flows" (Beechie et al. 2013). "the dam altered groundwater flow patterns over a large portion of the valley. In 2004, a second beaver dam built...steepened the groundwater flow gradient and create new surface water flow paths that inundated one quarter of the study area" (Westbrook et al. 2005). Thank you again for your comments and for your support!
Comment 02/29/2016 Type: 2 Commenter: Tyler Thompson
make sure your proposal is in the "proposed" section of the database or it will get missed in funding. It's currently listed as a "draft"
Comment 02/29/2016 Type: 2 Commenter: Heather Talley
Sorry about that, just made a few changes. Thank you for commenting to ensure it was in the "proposed" section!
Comment 09/27/2017 Type: 2 Commenter: Alison Whittaker
Please enter any missing expenses on the Finance page, update final features and fill out the Completion Form ASAP. Completion reports were due August 31st. If you have any questions about this don't hesitate to contact me. Thanks.
Completion
Start Date:
07/01/2016
End Date:
06/30/2017
FY Implemented:
2017
Final Methods:
Three seasonal technicians were hired during this process; Selena Yardley, Hunter Mecham, and Jennifer Batty. Hunter was provided a seasonal vehicle through motorpool, Selena already has a DWR permanent truck, and Jennifer used vehicle reimbursements. From July first through August 15th, traps were set in Hatch, North Escalante, Hoosier Lake, Mammoth Creek, and Kingston Canyon. From May 17th through June 30th, traps were set in LaVerkin, Black Canyon, Fish Lake (Bowery Haven), Virgin, Monroe (private pond), and Bicknell Bottoms. Beavers were taken to the following translocation sites: Fish Creek and Cottonwood Creek (July-August), Deer Creek, Baker Spring, and Shingle Creek (May - June). The live traps used were Hancock or Koro style traps. Each trap was secured with a cable and rebar stake, and baited with gland or lure and vegetation. Traps were checked each morning, and reset for the following evening. Before each site was trapped, notes were made about the complaint in a Google Form as well as an Excel spreadsheet for record keeping. Heather contacted Forest Service, county commissioners, water masters, irrigators, and/or animal control depending on the trapping and release site, to gain support for the activity. Once a beaver was attained, Heather was called for instruction for which quarantine facility to utilize, which pens within the facility to use for pairing beavers, updates to those relocating if quarantining was extended, etc. Beavers were fed each day, had water changes done each morning, and mister systems turned on during the day. Once beavers were caught, arrangements were made with technicians and Forest Service to relocate the beavers. Beginning in May, all beavers were "processed;" meaning they were given tail transmitters, oxygen levels monitored, identified gender, measured, weighed and given an approximate age. We hope the VHF tail transmitters will show us survival and movement post translocation.
Project Narrative:
A total of 27 beavers were moved during this fiscal year, which is an increase over the 18 that were moved the previous year. With three technicians, we were able to trap a substantial increase in locations, allowing for more beavers to be trapped and an increase in public satisfaction since we were able to cater to all nuisance complaints.
Future Management:
Since we've acquired the VHF transmitters, we plan to continue to track the signals to better assess survival and telemetry. Though we would like to utilize GPS telemetry, it would be almost completely ineffective (ATS quotes "three percent success rate") due to beavers being under water and in lodges so much of the time. If beavers move to nuisance locations, we will attempt to live-trap and release them in a low-conflict area. Other considerations for ameliorating nuisance situations could be flow control devices, and disseminating other information about avoiding conflicts with beavers.
Map Features
ID Feature Category Action Treatement/Type
1019 Other point feature
Project Map
Project Map