Mcgowan Mountain

The McGowan Mountain roadless area encompasses 10,504 acres across the high ridges and deep hollows of the central Monongahela National Forest. Three peaks—Stuart Knob (4,006 ft), Bickle Knob (4,003 ft), and McGowan Mountain (3,912 ft)—form the backbone of this terrain, with Baker Sods (3,146 ft) marking lower elevations to the south. The landscape drains northward into the Haddix Run-Shavers Fork headwaters system, a network of cold-water tributaries including Boar Run, Canoe Run, Clifton Run, Johns Run, Little Black Fork, and a dozen other named streams that converge to form Shavers Fork. These streams originate in the high coves and seeps of the ridgelines and flow through narrow valleys carved into the bedrock, creating the hydrological spine that sustains the area's forest communities.

Three distinct forest communities occupy different elevations and aspects across McGowan Mountain. The highest ridges and exposed slopes support Central Appalachian Dry Oak-Pine Forest, where red spruce (Picea rubens) and eastern hemlock (Tsuga canadensis) grow alongside mountain laurel (Kalmia latifolia) in the understory. The mid-elevation slopes transition to Appalachian-Allegheny Northern Hardwood Forest, dominated by sugar maple (Acer saccharum) and yellow birch (Betula alleghaniensis) with a diverse understory of striped maple (Acer pensylvanicum), hobblebush (Viburnum lantanoides), and herbaceous species including painted trillium (Trillium undulatum), bluebead lily (Clintonia borealis), and mountain woodsorrel (Oxalis montana). The cool, moist coves along the stream valleys support Central Appalachian Hemlock-Northern Hardwood Forest, where eastern hemlock dominates the canopy and the forest floor hosts specialized plants: the federally threatened small whorled pogonia (Isotria medeoloides), Shriver's frilly orchid (Platanthera shriveri), and American ginseng (Panax quinquefolius), a vulnerable species (IUCN) that has been harvested historically throughout Appalachia.

The area's wildlife reflects the diversity of its forest structure and cold-water streams. The federally endangered gray bat (Myotis grisescens), Indiana bat (Myotis sodalis), and northern long-eared bat (Myotis septentrionalis) roost in the hemlock and hardwood forests and forage over the streams at dusk. The federally endangered rusty patched bumble bee (Bombus affinis) pollinates flowering plants in the understory and canopy gaps. Brook trout (Salvelinus fontinalis) inhabit the headwater streams, where they feed on aquatic invertebrates and serve as prey for the bald eagle (Haliaeetus leucocephalus), which hunts along the larger waterways. The golden-winged warbler (Vermivora chrysoptera), a near-threatened species (IUCN), nests in early-successional areas and forest edges. Salamanders—including the federally threatened Cheat Mountain salamander (Plethodon nettingi) and Allegheny Mountain dusky salamander (Desmognathus ochrophaeus)—occupy the leaf litter and seepage areas of the hemlock coves, where moisture remains high year-round.

Walking through McGowan Mountain, a visitor experiences the landscape as a series of ecological transitions. Following a trail up from the valley floor, the forest begins in hemlock-dominated coves where the canopy is dense and the air cool and humid, the sound of running water constant from the nearby streams. As elevation increases, the hemlock gives way to mixed hardwoods, the understory opens, and light reaches the forest floor where trilliums and orchids bloom in spring. Climbing onto the ridgelines, the forest becomes more open and wind-exposed, with red spruce and mountain laurel dominating, views extending across the surrounding ridges. Descending into another drainage—perhaps Boar Run or Johns Run—the forest darkens again as hemlock reclaims the coves, and the cycle repeats. The streams themselves are the connective tissue: cold, clear water flowing downslope through narrow valleys, their banks lined with yellow birch and hemlock, their pools and riffles supporting the brook trout and aquatic life that sustains the larger food web.

Indigenous peoples utilized the diverse ecosystems of the Monongahela region for thousands of years. Lithic scatters, including chert flakes from stone tool sharpening, document temporary hunting camps and tool maintenance sites throughout the Monongahela National Forest. The region supported the Monongahela Culture, a proto-historic group that flourished approximately 900–1625 AD, though their exact tribal affiliation with modern nations remains debated among archaeologists. By the time European explorers arrived, permanent Indigenous settlements had largely been abandoned due to conflict and disease. However, the region remained vital to multiple nations: the Shawnee maintained hunting grounds in the Allegheny Mountains and river valleys; the Haudenosaunee, particularly the Seneca and Mingo, controlled trade and travel corridors; and the Cherokee used the southern and central highlands for seasonal hunting. The Seneca Trail, which passes near McGowan Mountain, served as a critical north-south thoroughfare connecting northern Haudenosaunee nations to southern groups. By the seventeenth and eighteenth centuries, the high Allegheny plateau functioned as shared hunting grounds contested by the Shawnee, Iroquois, and Cherokee, who fiercely resisted European settlement to protect these resources. The Beaver Wars of the seventeenth century and subsequent westward displacement pushed many tribes, including the Delaware, from their traditional territories in north-central West Virginia.

Between 1897 and 1914, the slopes of McGowan Mountain and the adjacent Otter Creek drainage underwent nearly complete clear-cutting. The Otter Creek Boom and Lumber Company served as the primary industrial operator, harvesting virgin red spruce and hardwoods using a network of narrow-gauge logging railroads and Climax and Shay geared steam locomotives. The Elklick Lumber Company operated a single-band sawmill near the mouth of Elklick Run beginning in 1902, harvesting timber from the western side of McGowan Mountain until 1911. Industrial facilities nearby, including tanneries in Parsons and a large pulp mill, processed hemlock and chestnut oak bark stripped from the surrounding mountains. Logging camps and slash piles filled the mountain's hollows during peak extraction. Beyond timber harvest, the Otter Creek Boom and Lumber Company operated small mines between 1897 and 1908 to produce fuel for its logging locomotives and camps. Prospecting also targeted the Sewell coal bed on the T.J. Arnold estate on McGowan Mountain in the early twentieth century, with the Western Maryland Railroad assisting in surveying high-heating-value fuel reserves for its operations.

The Monongahela National Forest was established on April 28, 1920, when President Woodrow Wilson signed a proclamation creating the forest under the authority of the Weeks Act of 1911, which permitted the federal government to purchase private lands to protect the headwaters of navigable streams. The first acquisition, the Arnold Tract of 7,200 acres in Tucker County, was purchased from Thomas J. Arnold on November 26, 1915. At the time of the 1920 proclamation, the forest comprised approximately 54,000 acres of devastated and logged land. On January 8, 1927, the National Forest Reservation Commission approved an extension of the original proclamation boundary.

During the Great Depression, the forest underwent its most significant expansion. Between 1932 and 1942, acreage grew from approximately 262,000 to over 806,000 acres. During the 1930s, the Civilian Conservation Corps was highly active throughout the region, planting millions of trees on denuded slopes and constructing fire breaks and trails. In 1934, a portion of the McGowan Mountain area was designated as the Fernow Experimental Forest to study reforestation and timber management. By 2009, when the Omnibus Public Lands Management Act added 698 acres on the northern and eastern flanks of McGowan Mountain to the Otter Creek Wilderness, the Monongahela National Forest had grown to over 920,000 acres. McGowan Mountain is now a 10,504-acre Inventoried Roadless Area protected under the 2001 Roadless Area Conservation Rule and managed within the Cheat Ranger District.

Vital Resources Protected

Headwater Network for Cold-Water Fisheries

McGowan Mountain's 10,504 acres encompass the headwaters of Haddix Run and Shavers Fork, along with 14 tributary streams that form the foundation of the Cheat River basin's aquatic ecosystem. These high-elevation headwaters maintain the cold, clean water chemistry required by native fish species, including the Candy Darter, which depends on stable spawning substrate in lower reaches fed by these streams. The roadless condition preserves the intact riparian forest canopy that regulates stream temperature and prevents sedimentation—both critical for species already stressed by historic acid deposition that has depleted soil buffering capacity and increased aluminum toxicity in high-elevation waters.

Bat Hibernacula and Summer Roosting Habitat

The area provides essential summer roosting habitat for three federally endangered bat species—the gray bat, Indiana bat, and northern long-eared bat—as well as the federally endangered Virginia big-eared bat and the proposed endangered tricolored bat. These species depend on large-diameter snags and mature forest structure within unfragmented interior forest to find the insect prey and thermal refugia they require during breeding season. Road construction would fragment this habitat and trigger edge effects that reduce insect availability; the loss of canopy continuity would also expose bats to increased predation risk and temperature stress during critical reproductive periods.

High-Elevation Climate Refugia for Cold-Adapted Species

McGowan Mountain's peaks—including Stuart Knob (4,006 ft) and Bickle Knob (4,003 ft)—anchor a landscape where northern hardwood and hemlock-dominated forests create a steep elevational gradient essential for species facing upslope squeeze from warming temperatures. The federally threatened Cheat Mountain salamander, found in high-elevation spruce-fir and northern hardwood forests within the area, depends on this intact elevational connectivity to track suitable microclimates as conditions warm. The roadless condition maintains the continuous forest structure that allows this and other cold-adapted species—including populations of eastern hemlock (near threatened, IUCN) and American chestnut (critically endangered, IUCN)—to persist in refugial pockets without the thermal disruption and fragmentation that roads would introduce.

Pollinator and Plant Diversity in Appalachian Hardwood Forests

The area's three distinct forest types—Appalachian-Allegheny Northern Hardwood Forest, Central Appalachian Dry Oak-Pine Forest, and Central Appalachian Hemlock-Northern Hardwood Forest—support specialized plant and pollinator communities including the federally endangered rusty patched bumble bee and the federally threatened small whorled pogonia, as well as the critically imperiled Shriver's frilly orchid and vulnerable American ginseng. These species depend on the structural complexity and microhabitat diversity of mature, unfragmented forest. Road construction would create edge habitat that favors invasive species like garlic mustard, which outcompetes native wildflowers and disrupts the flowering phenology that pollinators depend on for sustained nectar availability.

Threats from Road Construction

Sedimentation and Stream Temperature Increase from Canopy Removal

Road construction requires removal of riparian forest canopy along stream corridors to accommodate cut slopes, fill, and drainage infrastructure. This canopy loss directly increases water temperature by eliminating shade, harming the cold-water chemistry that native fish species and aquatic macroinvertebrates require for survival and reproduction. Simultaneously, exposed cut slopes and disturbed soil along the road corridor generate chronic sedimentation that smothers spawning substrate in downstream reaches, directly preventing the Candy Darter and other benthic species from successfully reproducing. In a watershed already stressed by acid deposition that has reduced soil buffering capacity, the combination of temperature increase and sedimentation would degrade water quality beyond the recovery capacity of these sensitive species.

Habitat Fragmentation and Edge-Effect Expansion for Forest-Interior Species

Road construction fragments the unfragmented interior forest that bats and other forest-dependent species require, creating edges where canopy closure is reduced and microclimate becomes warmer and drier. For the three federally endangered bat species that roost in large-diameter snags within the roadless area, fragmentation reduces the continuous habitat patch size below the threshold these species need to forage efficiently and avoid predators. The expanded edge habitat also favors invasive species and increases nest predation pressure on ground-nesting birds like the golden-winged warbler (near threatened, IUCN), which requires large interior forest patches to maintain viable populations.

Culvert Barriers and Hydrological Disruption to Elevational Connectivity

Road construction across the steep terrain of McGowan Mountain requires culverts to cross tributary streams. These structures act as barriers to aquatic organism passage, fragmenting populations of native fish and macroinvertebrates that depend on moving between high-elevation headwaters and lower reaches. More critically, culverts disrupt the natural hydrological connectivity that allows cold-adapted species like the Cheat Mountain salamander to track suitable microclimates along the elevational gradient as temperatures warm. Once this connectivity is severed, populations become isolated in shrinking refugial patches and lose the ability to shift their range upslope—a critical adaptation to climate change in high-elevation ecosystems.

Invasive Species Establishment and Spread via Road Corridors

Road construction creates a disturbed corridor of bare soil and early-successional vegetation that serves as a dispersal pathway for invasive species including garlic mustard, hemlock woolly adelgid, and emerald ash borer. The hemlock woolly adelgid is particularly threatening to the eastern hemlock stands in riparian corridors that provide thermal regulation and structural complexity for aquatic and forest-dependent species. Once established along a road corridor, invasive species spread into adjacent intact forest, degrading the native plant community that supports the specialized pollinators and understory plants—including American ginseng and Shriver's frilly orchid—that depend on the chemical and structural integrity of mature Appalachian hardwood forests.

Hiking and Trail Access

The McGowan Mountain Roadless Area offers four maintained trails ranging from 1.2 to 4.1 miles, all on native material surfaces. Yellow Creek Trail (135) is the shortest at 1.2 miles with intermediate difficulty—a blue-rated single-track with grades averaging 4% and maxing at 10%. Access starts at Yellow Creek Trailhead.

Moore Run Trail (138) covers 4.1 miles and is the most challenging. It follows an old logging railroad grade through thick brush and rock slides, with waist-deep creek crossings required. The trail passes through two high mountain meadows in its first two miles, then descends steeply alongside Moore Run—a Class 2–4 whitewater stream with 4- to 6-foot boulder drops—before terminating at Otter Creek. This trail is not suitable for mountain bikes. Access is from Moore Run Trailhead or Condon Run Trailhead.

McGowan Mountain Trail (136) is 3.9 miles and primarily used by hikers. Middle Point Trail (140) extends 3.5 miles along Forest Road 91 west of Stuart Campground. Both trails provide high-elevation access into the adjacent 20,698-acre Otter Creek Wilderness. A 5-mile section of the Allegheny Trail (701) is accessible via Forest Road 324 near Moore Run Trailhead.

Bickle Knob Observation Tower, a 1933 Civilian Conservation Corps structure at 4,003 feet, sits on Forest Road 91A and offers 360-degree views of the surrounding forest and Randolph County. Stuart Memorial Drive (Forest Road 91) is typically open mid-April through late autumn when snow-free. Trails here are often unblazed and lightly maintained; expect significant rhododendron overgrowth, swampy patches, and hidden obstacles. Mountain biking is prohibited on trails entering Otter Creek Wilderness but is permitted on non-wilderness trails and forest roads within the roadless area. Horseback riding is documented as a permitted use on the backwoods road and trail system.

Hunting

The McGowan Mountain Roadless Area is managed as part of the Otter Creek Wildlife Management Area under a cooperative agreement between the U.S. Forest Service and West Virginia Division of Natural Resources. American black bear, white-tailed deer, and wild turkey are documented game species. Small game includes gray, black, and fox squirrels; ruffed grouse; bobwhite quail; cottontail rabbit; and snowshoe hare. Bobcat, fisher, beaver, and otter are available for trapping.

A National Forest Hunting License (Class I) is required in addition to standard base licenses. For 2025–2026, deer seasons include archery/crossbow (Sept. 27–Dec. 31), buck firearms (Nov. 24–Dec. 7), and muzzleloader (Dec. 15–21). Black bear archery/crossbow runs Sept. 27–Dec. 31; firearms seasons vary by county. Wild turkey seasons are typically October (fall) and April–May (spring). The Mountaineer Heritage Season (mid-January) permits primitive weapons—longbows, recurve bows, and flint-lock/percussion cap muzzleloaders—for deer, bear, and turkey. All harvested big game must be electronically registered through the WVDNR system.

The roadless character of this area is essential to its hunting value. The backcountry terrain and minimal trail maintenance require experienced navigation and reward hunters seeking solitude away from developed access. The area adjoins Otter Creek Wilderness, creating a larger contiguous ecosystem for wide-ranging species like black bear. Access points include Forest Road 18 (northern edge), Forest Road 717 (western edge), and the extensive trail system traversing McGowan Mountain. Developed campsites are available at Stuart Campground and Stuart Group Campground.

Fishing

Shavers Fork, the primary fishable water bordering the area, supports rainbow, brown, brook, and golden rainbow trout, as well as smallmouth bass, rock bass, and largemouth bass. Haddix Run and smaller high-gradient tributaries support wild native brook trout. The Upper Shavers Fork is one of the most heavily stocked streams in West Virginia, receiving weekly stocking of rainbow, brook, brown, and golden rainbow trout during spring (January through May/early June) and a two-week period in October. Shavers Fork is a designated site for the West Virginia Gold Rush, where golden rainbow trout are specifically released.

A 5.5-mile section of Shavers Fork from the mouth of Whitmeadow Run downstream to McGee Run operates under delayed harvest regulations: catch-and-release only from November 1 through May 15 using only artificial flies and lures made of metal, wood, feathers, hair, or synthetic materials (Power Bait prohibited). General regulations apply May 16 through October 31. Anglers 15 and older must possess a valid West Virginia fishing license and trout stamp.

Access to the remote catch-and-release section is via Forest Road 92. Bemis and Cheat Bridge serve as common access points for the Upper Shavers Fork. Interior fishing requires foot travel from perimeter forest roads. The roadless condition preserves the remote character of the upper sections, offering a more wild and solitary angling experience compared to heavily trafficked roadside sections. The area's rugged, rock-strewn terrain features large deep pools and boulders; waders and felt-soled boots are recommended.

Birding

The high-elevation red spruce and northern hardwood ecosystems around McGowan Mountain and Stuart Knob support northern-affiliated species including Swainson's thrush, hermit thrush, veery, winter wren, golden-crowned kinglet, and red-breasted nuthatch. Bald eagles are documented in the area. The golden-winged warbler is present; the adjacent Fernow Experimental Forest is specifically managed for early successional species including golden-winged and mourning warblers.

During breeding season, the area hosts black-throated blue warbler, black-throated green warbler, Canada warbler, magnolia warbler, Blackburnian warbler, ovenbird, and Louisiana waterthrush. Fall migration brings raptors to high-elevation observation points. Winter residents include dark-eyed junco, purple finch, and occasionally red crossbill.

Bickle Knob Observation Tower at 4,003 feet provides eye-level views of forest birds and 360-degree vantage for observing migrating hawks, eagles, and falcons. Stuart Memorial Drive (Forest Road 91) traverses iconic red spruce forests and provides roadside birding access. Otter Creek Trail, an 11.8-mile route following the eastern base of McGowan Mountain, is documented for ruffed grouse, wild turkey, and wood warblers. Baker Sods, a 17-acre wildlife habitat improvement area, benefits birds through native plantings and maintained openings. Olson Observation Tower at the end of Forest Road 717 provides views of the McGowan Mountain ridge for raptor and forest bird observation. The area falls within or near the Elkins and Canaan Valley Christmas Bird Count circles.

Paddling

Shavers Fork, which forms a significant boundary and drainage of the area, is a major destination for kayaking, canoeing, and rafting—the highest large stream east of the Rocky Mountains and one of the most remote rivers in the region. The Bemis to Stuart Recreation Area section is rated Class III over 10 miles. The Stuart Recreation Area to Parsons stretch covers 26 miles at Class I–II, suitable for intermediate open canoe or beginner whitewater. The Bowden to Little Black Fork Bridge section is 14.6 miles at Class I–II; Little Black Fork Bridge to Parsons is 15.9 miles at Class I–II.

Stuart Recreation Area, located approximately 6 miles northeast of Elkins at the junction of WV Route 6 and Forest Road 91, is the primary put-in and take-out with developed river access. Bemis (CR 22 bridge) and Bowden (Faulkner Road bridge) serve as additional access points. Parsons (US 119 bridge) is a well-maintained take-out with a Cheat River Water Trail parking lot.

Paddling is rain-dependent with the most reliable window from February through May. The Cheat Bridge gauge is used for upper sections; recommended levels are 5.5 to 6.5. The river is part of the Upper Cheat River Water Trail, a 40-mile calm-water segment from Parsons to Rowlesburg. Shaver's Fork Adventures, LLC, based in Elkins, provides tube, kayak, and canoe rentals and shuttle services. The roadless condition preserves the remote character of the upper Shavers Fork, offering paddlers access to undeveloped river corridors away from road-accessible sections.

Photography

Bickle Knob Observation Tower at 4,003 feet provides 360-degree panoramic views of the Allegheny Mountains and Randolph County. On clear days, Mount Storm smokestacks (Tucker County) and Shinnston smokestacks (Harrison County) are visible. The parking area at the tower base offers scenic vistas for those unable to climb. Stuart Memorial Drive (Forest Road 91) is a 10-mile scenic drive through red spruce forests and limestone geology, noted for luxurious roadside rhododendron blooms during flowering season.

Shavers Fork offers stream and water feature photography. The area's red spruce forests are primary subjects for forest interior photography. Bickle Knob is documented for sunrise and sunset photography and is an excellent vantage for wildlife viewing with binoculars. The remote, backcountry character of the high-elevation ridges provides minimal light pollution for dark sky and stargazing photography. The roadless condition preserves the undeveloped viewshed and forest character that make these scenic and photographic opportunities possible.