0418033

Ashley National Forest · Utah · 24,909 acres · RoadlessArea Rule (2001)
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Description

Area 0418033 is a 24,909-acre Inventoried Roadless Area on the Ashley National Forest in Utah, occupying a mountainous, montane position in Duchesne and Wasatch counties. The terrain is scored by a series of hollows, canyons, and ridges — Beaver Canyon, Bumper Canyon, Calf Hollow, Sulfur Draw, and Shotgun Draw — that converge toward the headwaters of the Strawberry River, one of the upper Uintah Basin's most significant drainages. The Right Fork White River and Minnie Creek trace parallel courses through the area's interior, fed in part by springs including Big Beaver Springs and Sagers Spring. Water originates high on Strawberry Peak and along Twelve Hundred Dollar Ridge, descending through Lost Canyon and Pine Hollow before entering the Beaver Canyon–Strawberry River system. At moderate elevations, this hydrology supports dense riparian corridors that form distinct habitat edges against the surrounding upland communities.

The dominant upland matrix across this area is Intermountain Mountain Sagebrush Steppe — a vast, wind-scoured community of basin big sagebrush and associated bunchgrasses that blankets the broad ridges and flats. Where cold air pools and snowpack lingers, Rocky Mountain Dry Subalpine Spruce-Fir Forest takes over, with stands of Engelmann spruce and subalpine fir shading a sparse understory. On slightly warmer, south-facing slopes and canyon walls, Rocky Mountain Gambel Oak Shrubland forms dense, nearly impenetrable thickets, its leaves turning deep red and orange in autumn. Rocky Mountain Aspen Forest claims mid-elevation basins and moist north-facing aspects, the white-barked trees forming clonal groves whose understory is carpeted by forbs in summer and defined by bright fall color. On the driest canyon rims and lower slopes, Colorado Plateau Pinyon-Juniper Woodland provides the characteristic two-tree silhouette of the Colorado Plateau transition zone. Streamside zones support Rocky Mountain Subalpine Streamside Woodland along the upper drainages and Rocky Mountain Foothill Streamside Woodland at lower elevations, with narrowleaf cottonwood and willow fringing the named creeks. Great Basin Subalpine Bristlecone Pine Woodland occupies the most exposed, wind-battered ridgetop sites — this woodland is among the oldest plant communities in North America, with individual trees routinely exceeding 1,000 years.

The aspen groves and subalpine meadows support Clark's nutcracker (Nucifraga columbiana), which harvests and caches whitebark pine seeds, functioning as an essential dispersal agent across the high-elevation forest margin. In the dense spruce-fir canopy, flammulated owls (Psiloscops flammeolus) take moths and beetles at night. Broad-tailed hummingbirds (Selasphorus platycercus) track the bloom progression of scarlet skyrocket (Ipomopsis aggregata) as it moves upslope through summer, while mule deer (Odocoileus hemionus) browse wax currant (Ribes cereum) in the shrubby transition zones. The Strawberry River system and its tributaries sustain Rocky Mountain cutthroat trout (Oncorhynchus virginalis) in cold, well-oxygenated reaches, with brown trout (Salmo trutta) occupying lower, warmer pools. Moose (Alces alces) wade the willowed margins of Minnie Creek and the headwater springflows. Golden eagles (Aquila chrysaetos) hunt the open sagebrush and meadow benches, riding thermals over the canyon rims. The terrestrial gartersnake (Thamnophis elegans) moves between wet meadow margins and the dry shrub-steppe, bridging aquatic and upland food webs. Portions of this area fall within the potential range of several federally listed species; see the Conservation section for details.

A route descending from Strawberry Peak into Beaver Canyon passes through nearly every community type in compressed vertical sequence. The upper ridgeline moves through open sagebrush and a few exposed bristlecone pines, the wind audible even on calm days. Dropping into the north-facing head of Beaver Canyon, the canopy closes into spruce-fir, the air noticeably cooler, the ground softened by duff. The transition into aspen — abrupt, marked by a change in light quality from green-gray to luminous yellow-white — coincides with the sound of Minnie Creek below. Lower in Calf Hollow, the canyon walls tighten and Gambel oak scrapes the trail margins. At the confluence of draws near the canyon floor, streamside cottonwood and willow signal the return of open sky, and the water rushing over cobble at Big Beaver Springs carries the accumulated drainage of the entire upper watershed.

History

The lands that now form the Ashley National Forest's Duchesne Ranger District have sustained human presence for more than twelve thousand years. The Paleoindian period represents the earliest occupation of the Ashley National Forest, commencing around 10,000 BC and concluding around 6,500 BC, with those early inhabitants following herds of now-extinct megafauna [1]. Archaic-era foragers succeeded them across roughly eight thousand years, and by approximately AD 100 the Fremont culture had taken root in northeastern Utah, introducing corn cultivation, ceramic vessels, and permanent pithouses in the Uinta Basin lowlands [1].

Between AD 1300 and AD 1600, the Fremont pattern gave way to a more mobile hunting-and-gathering economy, whose practitioners are most likely the direct ancestors of the Ute and Shoshone peoples encountered by Euro-American explorers in later centuries [1]. The Ute Nation once covered most of Utah, Colorado, and northern New Mexico, maintaining control over the region's richest natural resources for thousands of years [3]. Three bands ultimately composed the Northern Ute tribe: the Whiteriver, Uncompahgre, and Uintah; the Uintah Band was first to call the Uintah Basin their home [2]. After a series of conflicts with arriving Mormon settlers, the Utes signed the Treaty of Spanish Fork in 1865 and were forced to move to the dry Uintah Basin [2]. The Uintah Reservation had been created in 1861 by President Abraham Lincoln as a permanent home for the Uintah and White River Utes [4]. In 1881, the U.S. government forced the White River Utes from Colorado to the Uintah Reservation; the following year it created the adjacent Ouray Reservation, which was later consolidated with the Uintah [2]. By 1882, the several Ute bands had been pushed off their wide-ranging lands into reservations in the Uintah Basin of eastern Utah [3].

Euro-American cattlemen and sheepherders arrived in the Uinta Basin well before homesteaders. Parson Dodds, the first Indian agent on the Uintah Valley Reservation, brought cattle to the area in 1868, and grazing on the Uinta Mountains soon became the primary impetus for Euro-American settlement [1]. Timber harvesting followed: the first substantial logging on what would become the Ashley National Forest reportedly occurred in 1877 on Taylor Mountain, and in 1880 Alma Johnstun brought the first sawmill to the area, transporting it from Park City to Dry Fork Mountain [1]. Mining also shaped the eastern Uintas during this era; the largest operation manifested after copper ore was discovered on Dyer Peak in the 1880s, and a copper smelter was built in 1899 on Anderson Creek at the toe of Dyer Peak's eastern slope [1]. On August 27, 1905, the former Uintah Reservation was opened to homesteading under the federal Homestead Act — the last region in Utah settled by Euro-Americans — and 160-acre parcels were claimed across Duchesne County [4, 6].

Federal administration of these lands had already begun. President Grover Cleveland created the Uintah Forest Reserve on February 22, 1897, drawing from un-allotted public lands formerly within the Uintah Valley Indian Reservation [1]. On July 1, 1908, President Theodore Roosevelt signed Executive Order 884, establishing the Ashley National Forest with 952,086 acres carved from the Uinta National Forest [1]. By 1914, the new national forest permitted 96,110 sheep and 18,000 cattle and horses on its ranges [1]. The Great Depression brought another transformation: in 1933 the Ashley National Forest received two of Utah's first Civilian Conservation Corps camps, and CCC enrollees subsequently constructed guard stations, telephone lines, drift fences, and the Ute Mountain Fire Lookout Tower — completed between 1936 and 1937 — that still stands today [1, 5].

Conservation: Why Protection Matters

Vital Resources Protected

Headwater Stream Integrity

The Beaver Canyon–Strawberry River headwaters, Right Fork White River, and Minnie Creek originate within this roadless area, sustained by named springflows at Big Beaver Springs and Sagers Spring. In a roadless condition, the Rocky Mountain Subalpine Streamside Shrubland and Rocky Mountain Foothill Streamside Woodland communities that line these drainages remain intact — root systems, canopy shading, and organic matter inputs that keep headwater temperatures cold, sediment loads low, and channel substrate stable. The Strawberry River feeds the Colorado River system, meaning the integrity of these headwaters is consequential for aquatic connectivity across a much larger basin.

Elevational Gradient Connectivity

Area 0418033 contains an unusually complete elevational sequence: from Intermountain Salt Desert Scrub and Semi-Desert Shrub-Steppe at lower elevations through Great Basin Big Sagebrush Shrubland, Rocky Mountain Gambel Oak Shrubland, Aspen Forest, Subalpine Spruce-Fir Forest, Rocky Mountain Subalpine Meadow, and Great Basin Subalpine Bristlecone Pine Woodland at the exposed ridgetops. This gradient allows species to shift ranges in response to drought cycles and seasonal variation without crossing developed land. Great Basin Subalpine Bristlecone Pine Woodland — one of the world's longest-lived plant communities, with individual trees exceeding 1,000 years — occupies the most stress-exposed ridgetop sites, where undisturbed soils and minimal anthropogenic disturbance are prerequisites for persistence.

Interior Sagebrush-Steppe Habitat

Intermountain Mountain Sagebrush Steppe, the dominant cover type across the area's broad ridges and flats, requires large, unfragmented blocks to maintain its characteristic structure and wildlife function. This community retains intact biological soil crusts — thin, living layers of cyanobacteria, lichens, and mosses that suppress invasive annual grass establishment, reduce erosion, and fix nitrogen. Once ground disturbance removes or compacts this crust, cheatgrass (Bromus tectorum) and other invasive annuals can establish rapidly, initiating a conversion cycle that alters the fire return interval from decades to years and prevents sagebrush recovery.

Potential Effects of Road Construction

Sediment Loading in Headwater Drainages

Road construction on steep canyon terrain — the slopes descending into Beaver Canyon, Bumper Canyon, Calf Hollow, and Sulfur Draw — generates cut slopes and fill slopes that erode continuously for decades following construction. Sedimentation raises streambed elevations, fills interstitial gravel essential for aquatic invertebrate communities, and delivers fine particles that reduce the cold, clear-water conditions in the Strawberry River headwaters. These effects persist well after construction ends because bare cut faces lack the root systems and soil structure required to restore erosion resistance.

Invasive Annual Grass Establishment

Road corridors through Intermountain Mountain Sagebrush Steppe and Rocky Mountain Gambel Oak Shrubland act as dispersal vectors for cheatgrass and other invasive annuals, which travel as hitchhikers on vehicle tires and in fill and gravel material. Once established in the disturbed roadbed margin, these species spread into the adjacent sagebrush matrix and alter the fire regime from multi-decade intervals to annual or biennial cycles — a frequency that kills mature sagebrush shrubs but favors annual grass recovery. Road construction creates a linear inoculation route across an otherwise intact landscape that currently lacks persistent establishment points.

Fragmentation of Elevational Movement Corridors

This area's function as a climate-gradient movement corridor depends on continuous undisturbed habitat from lower shrub-steppe zones to subalpine ridgetops. Road construction introduces hard barriers — active vehicle traffic, chronic noise, edge effects, and light intrusion — that interrupt daily and seasonal wildlife movement across the elevational gradient. Once fragmented, the Great Basin Subalpine Bristlecone Pine communities near ridgelines and the Subalpine Spruce-Fir stands below them become isolated patches with reduced capacity to receive recruits from connected populations, compressing the very gradient that makes the area function as a refugium under variable climate conditions.

Federally Listed Species

The following ESA-listed species fall within the potential range of this roadless area:

  • Bonytail (Gila elegans): Endangered
  • Colorado pikeminnow (Ptychocheilus lucius): Endangered
  • Razorback sucker (Xyrauchen texanus): Endangered
  • Humpback chub (Gila cypha): Threatened
  • Mexican spotted owl (Strix occidentalis lucida): Threatened
  • Suckley's cuckoo bumble bee (Bombus suckleyi): Proposed Endangered
  • Monarch butterfly (Danaus plexippus): Proposed Threatened
Recreation & Activities

Trails

Area 0418033 on the Ashley National Forest in Utah includes seven documented trails totaling more than 31 miles, all on native material surfaces. Three trails are designated for hikers: Bull Hollow Trail (0086) at 3.4 miles, Slab Canyon Trail (1088) at 6.7 miles, and Shotgun Trail (1085) at 4.0 miles. Two are designated for equestrian use: Cow Hollow Trail (1089), the longest in the area at 9.9 miles, and Pine Hollow-Minnie Creek Trail (1090) at 3.9 miles. French Hollow Trail (3027, 3.5 miles) and the short Little Rabbit Long Ridge Loop (1105, 0.1 miles) round out the network.

Slab Canyon offers the most substantial hiking experience, traversing 6.7 miles through the canyon bearing its name — a route that moves through Rocky Mountain Gambel Oak Shrubland on the lower slopes, transitioning to Aspen Forest in the mid-reaches, before opening into the broader terrain above. Shotgun Trail (4.0 miles) and Bull Hollow Trail (3.4 miles) provide access to the interior canyon terrain from different approach angles. No maintained trailheads are documented for this area, and no developed campgrounds are present; access and camping are dispersed in character, consistent with the area's roadless designation.

Equestrian Recreation

The Cow Hollow Trail (1089) at 9.9 miles is the primary equestrian route, following Cow Hollow through the sagebrush steppe and lower forest communities on native-surface tread. The Pine Hollow-Minnie Creek Trail (1090) offers a 3.9-mile route that connects Pine Hollow to the Minnie Creek drainage, making it viable as part of a longer point-to-point equestrian outing. The native-material surfaces of both trails, free of the drainage problems that accompany road construction, maintain the firm but yielding footing that stock travel requires.

Fishing

The Strawberry River headwaters, Right Fork White River, and Minnie Creek flow through this roadless area, all accessible from the trail system. Rocky Mountain cutthroat trout (Oncorhynchus virginalis) hold in the colder, higher-gradient reaches; brown trout (Salmo trutta) are documented in lower, warmer pools; and rainbow trout (Oncorhynchus mykiss) are present in the system. Big Beaver Springs and Sagers Spring contribute baseflow that sustains fish-holding stretches through the drier months. The Strawberry River system connects downhill to Strawberry Reservoir, one of Utah's major fisheries, and the water quality maintained by the roadless watershed directly supports those downstream conditions.

Wildlife and Birding

Moose (Alces alces) use the willowed margins of Minnie Creek and the headwater spring areas — a relatively recent range expansion for moose in Utah that now makes them a documented presence in the Strawberry watershed. Mule deer (Odocoileus hemionus) range through the sagebrush-steppe and shrubland communities throughout the area. The nearby Strawberry Reservoir eBird hotspots — the most active recording 152 species across 145 checklists — document the broader bird diversity of the watershed, which includes species that move between the reservoir and the upland habitats of this roadless area. The elevational gradient from semi-desert scrub to subalpine makes the area productive for birding across seasonal transitions, particularly during spring and fall migration when the aspen groves and canyon bottoms concentrate passerines.

What the Roadless Condition Makes Possible

The recreation here depends directly on the absence of roads. Slab Canyon's 6.7 miles remain quiet enough for the moose that wade its stream margins; Minnie Creek's cutthroat trout hold in water that no roadside erosion has sedimented; the Cow Hollow equestrian route covers nearly 10 miles without a single motorized crossing. No developed campgrounds means that overnight use disperses across the landscape rather than concentrating at paved pullouts, and the intact sagebrush matrix means no cheatgrass-invaded roadsides displace the native vegetation along the trail corridors. These are not incidental benefits — they are the functional basis of recreation in a 24,909-acre montane roadless area on the Ashley National Forest.

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Observed Species (16)

Species with confirmed research-grade observation records from iNaturalist community science data.

Broom Snakeweed (1)
Gutierrezia sarothrae
Brown Trout (5)
Salmo trutta
Clustered Leatherflower (1)
Clematis hirsutissima
Common Mullein (1)
Verbascum thapsus
Hoary Tansy-aster (1)
Dieteria canescens
Moose (1)
Alces alces
Mule Deer (1)
Odocoileus hemionus
Rainbow Trout or Steelhead (1)
Oncorhynchus mykiss
Rocky Mountain Cutthroat Trout (2)
Oncorhynchus virginalis
Scarlet Skyrocket (1)
Ipomopsis aggregata
Sessile Water-speedwell (1)
Veronica catenata
Sockeye Salmon (1)
Oncorhynchus nerka
Terrestrial Gartersnake (1)
Thamnophis elegans
Virile Crayfish (1)
Faxonius virilis
Wax Currant (1)
Ribes cereum
Western Toad (1)
Anaxyrus boreas
Federally Listed Species (7)

Species identified by the U.S. Fish and Wildlife Service as potentially occurring within this area based on range and habitat data. These designations do not indicate confirmed presence — they identify habitat where agency actions may require consultation under the Endangered Species Act.

Bonytail
Gila elegansEndangered
Humpback Chub
Gila cyphaThreatened
Mexican Spotted Owl
Strix occidentalis lucidaThreatened
Colorado Pikeminnow
Ptychocheilus luciusE, XN
Monarch
Danaus plexippusProposed Threatened
Razorback Sucker
Xyrauchen texanusE, PT
Suckley's Cuckoo Bumble Bee
Bombus suckleyiProposed Endangered
Other Species of Concern (7)

Species identified by the U.S. Fish and Wildlife Service as potentially occurring based on range and habitat data.

Broad-tailed Hummingbird
Selasphorus platycercus
Clark's Nutcracker
Nucifraga columbiana
Evening Grosbeak
Coccothraustes vespertinus
Flammulated Owl
Psiloscops flammeolus
Golden Eagle
Aquila chrysaetos
Olive-sided Flycatcher
Contopus cooperi
Pinyon Jay
Gymnorhinus cyanocephalus
Migratory Birds of Conservation Concern (6)

Birds of conservation concern identified by the U.S. Fish and Wildlife Service as potentially occurring based on range data. These species may warrant additional consideration under the Migratory Bird Treaty Act.

Broad-tailed Hummingbird
Selasphorus platycercus
Clark's Nutcracker
Nucifraga columbiana
Evening Grosbeak
Coccothraustes vespertinus
Golden Eagle
Aquila chrysaetos
Olive-sided Flycatcher
Contopus cooperi
Pinyon Jay
Gymnorhinus cyanocephalus
Vegetation (19)

Composition from LANDFIRE 2024 EVT spatial analysis. Ecosystems classified per NatureServe Terrestrial Ecological Systems.

Intermountain Mountain Sagebrush Steppe
Shrub / Shrubland · 3,585 ha
GNR35.6%
GNR13.4%
Rocky Mountain Aspen Forest
Tree / Hardwood · 1,185 ha
GNR11.8%
Rocky Mountain Gambel Oak Shrubland
Shrub / Shrubland · 577 ha
GNR5.7%
Rocky Mountain Foothill Shrubland
Shrub / Shrubland · 496 ha
G34.9%
Colorado Plateau Mixed Bedrock Canyon and Tableland
Sparse / Sparsely Vegetated · 435 ha
4.3%
Rocky Mountain Cliff Canyon and Massive Bedrock
Sparse / Sparsely Vegetated · 393 ha
3.9%
Rocky Mountain Subalpine Meadow
Herb / Grassland · 391 ha
GNR3.9%
Intermountain Aspen and Conifer Forest
Tree / Conifer-Hardwood · 320 ha
G43.2%
Southern Rockies Mixed Conifer Forest
Tree / Conifer · 297 ha
GNR2.9%
Southern Rockies Mixed Conifer Forest
Tree / Conifer · 201 ha
GNR2.0%
GNR1.4%
GNR1.4%
Northern Rockies Subalpine Grassland
Herb / Grassland · 79 ha
GNR0.8%
Intermountain Semi-Desert Grassland
Herb / Grassland · 64 ha
G20.6%
G30.1%
G30.0%
Great Basin Big Sagebrush Shrubland
Shrub / Shrubland · 3 ha
G30.0%

0418033

0418033 Roadless Area

Ashley National Forest, Utah · 24,909 acres