

Mackey Mountain encompasses 5,934 acres of montane terrain in the Pisgah National Forest, with elevations ranging from approximately 3,200 feet at Buckeye Knob and Big Laurel Gap to 3,999 feet at Mackey Mountain's summit. The area drains into the Catawba River watershed through a network of named streams: Mackey Creek, Clear Creek, Bear Cave Branch, Laurel Fork Creek, Locust Creek, Sams Creek, and Sugar Cave Creek. These waterways originate on the ridges and slopes of Mackey Mountain, Narrows Knob, Chestnutwood Mountain, and Sams Ridge, flowing downslope through narrow valleys and gaps that channel water toward the Catawba system. The landscape's steep terrain and high precipitation create conditions where water moves rapidly from ridge to stream, carving distinct drainage patterns across the forest floor.
The forest composition shifts with elevation and moisture availability across the area. At higher elevations and on exposed ridges, Chestnut Oak Forest dominates, with chestnut oak (Quercus montana) and Table Mountain pine (Pinus pungens) forming an open canopy above a heath understory of mountain laurel (Kalmia latifolia) and galax (Galax urceolata). In the cooler, moister coves and north-facing slopes, Carolina Hemlock Forest and Acidic Cove Forest prevail, where Carolina hemlock (Tsuga caroliniana) and northern red oak (Quercus rubra) create a dense canopy. The understory in these coves includes mountain sweet pepperbush (Clethra acuminata), Fraser magnolia (Magnolia fraseri), and Carolina rhododendron (Rhododendron carolinianum), with a ground layer of blue Ridge bittercress (Cardamine flagellifera) and other shade-tolerant herbs. Rich Cove Forest occupies the most favorable microsites, where moisture and soil fertility support a more diverse assemblage. Montane Oak-Hickory Forest occurs on intermediate slopes, while Pine-Oak Heath characterizes drier ridgetops and south-facing aspects.
The area supports populations of federally endangered species dependent on these forest communities. The federally endangered gray bat (Myotis grisescens) and northern long-eared bat (Myotis septentrionalis) roost in caves and hollow trees throughout the forest, emerging at dusk to forage on insects above streams and clearings. Brook trout (Salvelinus fontinalis) inhabit the cold, clear headwater streams, their presence indicating water quality suitable for aquatic macroinvertebrates that form the base of the food web. Seal salamanders (Desmognathus monticola) occupy the splash zones and seepage areas along stream banks, while Yonahlossee salamanders (Plethodon yonahlossee) move through the leaf litter of cove forests. Black-throated blue warblers (Setophaga caerulescens) nest in the understory of hemlock and cove forests, hunting insects among the rhododendron and mountain laurel. The federally threatened bog turtle (Glyptemys muhlenbergii), similarity of appearance, inhabits seepage areas and small wetlands where moisture persists year-round. Several plant species of conservation concern occur here: the federally endangered Roan Mountain bluet (Hedyotis purpurea var. montana) and rock gnome lichen (Gymnoderma lineare), and the federally threatened small whorled pogonia (Isotria medeoloides), which depends on specific fungal associations in undisturbed forest soil.
A visitor moving through Mackey Mountain experiences distinct transitions as elevation and aspect change. Beginning in a Rich Cove Forest along Mackey Creek or Laurel Fork Creek, the forest is dense and dark, with hemlock and magnolia overhead and a thick understory of rhododendron and bittercress underfoot. The sound of flowing water is constant. As the trail climbs away from the creek and aspect shifts, the forest opens into Acidic Cove Forest, where the canopy becomes more mixed and light reaches the ground layer. Continuing upslope toward Sams Ridge or Mackey Mountain's summit, the forest transitions to Chestnut Oak Forest; the canopy thins, mountain laurel becomes dominant in the understory, and galax spreads across the forest floor. On the ridgeline itself, the view opens, the wind increases, and the forest becomes visibly lower and more sparse, with Table Mountain pine and exposed rock. Descending into a different drainage—perhaps toward Clear Creek or Bear Cave Branch—the sequence reverses: the forest darkens again, hemlock reappears, and the sound of water returns as the cove forest reclaims the landscape.


Native peoples inhabited the region surrounding Mackey Mountain for millennia. By the time of European contact around 1540, the Cherokee had established sophisticated agricultural systems in the broader region. The Cherokee used the high-elevation forests of this area for hunting game and gathering medicinal plants and food, including chestnuts and berries. Siouan-speaking groups, including the Saura, Sugaree, and Waxhaw, also inhabited the region before eventually merging with the Catawba Nation. The Catawba, historically known as the "People of the River," inhabited the Piedmont region and the Catawba River Valley, which extends into the area surrounding Mackey Mountain. Hikers and researchers have identified potential Cherokee trail trees—trees intentionally bent to serve as navigational markers—along the ridges of Mackey Mountain. In 1767, the Treaty of the Tryon Line established a boundary following the crest of the Blue Ridge Mountains, including the ridgelines of the Mackey Mountain area, intended to separate white settlers from Cherokee hunting grounds. During the Revolutionary War in 1776, General Griffith Rutherford led a militia of 2,400 men and Catawba allies from Davidson's Fort in a scorched-earth campaign to destroy Cherokee settlements.
Industrial-scale logging occurred throughout Western North Carolina in the late nineteenth and early twentieth centuries, but the upper reaches of Mackey Creek and Curtis Creek were largely bypassed because the terrain was too rugged for early twentieth-century logging crews to reach. Significant portions of the area are documented as having never been logged, preserving primary forest conditions that predate European settlement. No historical logging railroads, company towns, or large-scale industrial operations were established within the boundaries of this roadless area.
The Pisgah National Forest was established on October 17, 1916, by Presidential Proclamation 1347 signed by President Woodrow Wilson, becoming the first national forest in the eastern United States created from purchased land. The establishment was authorized by the Weeks Act of 1911, which empowered the federal government to purchase private lands to protect the watersheds of navigable streams. The first land purchase under the Weeks Act in the area occurred in March 1911, when 8,100 acres in the Curtis Creek watershed in McDowell County were acquired. The core of the forest was formed in 1914 when Edith Vanderbilt sold approximately 86,700 acres from the Biltmore Estate to the federal government. In 1954, the Pisgah National Forest was administratively combined with the Croatan and Nantahala National Forests to be managed collectively as the National Forests of North Carolina. In 1964, the Linville Gorge and Shining Rock areas within the forest were designated as original federal Wilderness areas.
Mackey Mountain is designated as a 5,934-acre Inventoried Roadless Area and is protected under the 2001 Roadless Area Conservation Rule. Today, the Eastern Band of Cherokee Indians is based in nearby Western North Carolina and, under the 2023 Land Management Plan for the Nantahala and Pisgah National Forests, partners with the U.S. Forest Service to co-manage resources and protect places of significance within these ancestral lands. The U.S. Forest Service recognizes the ancestral connections of the Cherokee Nation of Oklahoma, United Keetoowah Band of Cherokee Indians, Muscogee Creek Nation, and Tuscarora Nation to the Pisgah National Forest.

Headwater Protection for the Catawba River Basin
Mackey Mountain contains the headwaters of Mackey Creek and multiple tributary systems (Clear Creek, Bear Cave Branch, Laurel Fork Creek, Locust Creek, Sams Creek, Sugar Cave Branch) that feed into the Catawba River. The roadless condition preserves the intact riparian forest—including Carolina hemlock and eastern hemlock stands—that stabilizes streambanks, filters runoff, and maintains cool water temperatures essential for aquatic life. These headwaters currently function in proper condition according to USFS watershed assessments, a status that depends on the absence of road-related erosion and canopy disturbance upstream.
Bat Habitat Connectivity Across Elevation Gradients
The area supports three federally endangered bat species—gray bat, northern long-eared bat, and tricolored bat (proposed endangered)—that depend on continuous forest structure from the montane oak-hickory and cove forests at lower elevations to the Carolina hemlock forests at higher elevations. Roads fragment this vertical habitat corridor, creating isolated patches where bats cannot safely forage or commute between roosting and feeding areas. The roadless condition maintains the unbroken canopy structure these species require to navigate and hunt across the elevation gradient.
High-Elevation Rare Plant Refugia
Mackey Mountain's montane and high-elevation ecosystems harbor multiple federally protected plants found nowhere else in abundance: the roan mountain bluet and rock gnome lichen (both federally endangered), small whorled pogonia (federally threatened), and state-rare species including mountain goldenheather (critically imperiled) and Oconee bells (imperiled). These species occupy specific microsites on rocky outcrops and in acidic cove forests where soil chemistry and moisture regimes are finely balanced. Road construction and associated fill, drainage, and soil disturbance would directly destroy these localized populations, which cannot recolonize once lost.
Salamander and Herpetofauna Habitat in Intact Forest
The roadless area provides continuous moist forest habitat for southern Appalachian salamanders and common box turtles (vulnerable, IUCN), species highly sensitive to desiccation and fragmentation. The unbroken canopy and leaf litter layer maintain the cool, humid microhabitat these animals require year-round. Road construction removes canopy cover and creates drying edge effects that extend into adjacent forest, reducing the effective habitat available to these species across the entire roadless area.
Sedimentation and Stream Temperature Increase from Canopy Removal
Road construction requires cutting slopes and removing riparian forest to create roadbeds and sight lines. This exposes mineral soil to erosion, sending sediment into tributaries and smothering the clean gravel spawning substrate that native brook trout and other aquatic invertebrates depend on. Simultaneously, removal of hemlock and cove forest canopy along stream corridors allows direct sunlight to warm the water, raising temperatures above the narrow range tolerated by cold-water species. Because Mackey Mountain's streams originate within the roadless area, roads built here would degrade water quality at the source, affecting the entire downstream Catawba River system.
Habitat Fragmentation and Loss of Bat Commute Corridors
Road construction creates a linear clearing that fragments the continuous canopy bats require to move safely between roosting sites and foraging habitat. The three federally endangered bat species present—gray bat, northern long-eared bat, and tricolored bat—cannot cross open areas; they navigate by echolocation along forest edges and canopy structure. A road cuts this corridor into isolated patches, preventing bats from accessing the full range of elevations and forest types they need to find sufficient insects across seasons. Once fragmented, the habitat patches become too small to support viable populations, and the species cannot recolonize because the barrier persists.
Direct Destruction of Rare Plant Microsites and Soil Disturbance
Road construction and associated fill, grading, and drainage ditches directly destroy the specific soil and rock conditions where federally endangered plants like roan mountain bluet and rock gnome lichen survive. These species occupy narrow ecological niches—particular soil pH, moisture, and light conditions on high-elevation outcrops—that cannot be recreated. Once the roadbed and its associated disturbance zone eliminate these microsites, the plants are gone permanently from the area. The chronic erosion and altered hydrology from road drainage also destabilize the acidic cove forest soils where small whorled pogonia and other rare plants persist.
Invasive Species Establishment Along Road Corridors
Road construction creates disturbed soil and a linear corridor of light and disturbance that invasive plants exploit. Japanese honeysuckle, Oriental bittersweet, and Japanese stiltgrass—already documented as threats on the IRA's perimeter—would rapidly colonize the road corridor and adjacent edges, outcompeting native understory plants that salamanders, box turtles, and rare plants depend on. The road becomes a permanent vector for invasive spread into the previously intact forest interior, degrading habitat quality across a widening zone on both sides of the roadbed. Because the road persists indefinitely, so does the invasion pressure it creates.

The Mackey Mountain Roadless Area encompasses 5,934 acres of old-growth forest in the Pisgah National Forest's Grandfather Ranger District. Four maintained trails provide foot access to ridgelines, waterfalls, and remote headwater streams. The area's roadless condition preserves the backcountry character essential to each of these recreation opportunities — removing roads would fragment habitat, degrade water quality in wild trout streams, and eliminate the quiet, undisturbed experience that defines hiking and hunting here.
Hiking. Four trails offer access to the area's ridgelines and interior streams. The Hickory Branch Trail (TR213, 1.6 miles) begins at Curtis Creek Campground and follows Hickory Branch stream to a 30-foot waterfall, then climbs steeply toward Lead Mine Gap. The Lead Mine Gap Trail (TR212, 2.3 miles) traverses ridgeline terrain with short, steep pitches, topping out on Buckeye Knob at 3,398 feet and offering views of Table Rock, Hawksbill, and Grandfather Mountain. The Mackey Mountain Trail (TR216, 3.2 miles) is rated intermediate to difficult; the first 3 miles were rehabilitated by volunteers in 2021, but the final mile to the 3,999-foot summit remains unmaintained and difficult to follow. The Sugar Cove Trail (TR219, 2.5 miles) is steep, climbing from 2,962 to 3,354 feet. A popular loop combines Hickory Branch and Lead Mine Gap trails with a walk down Curtis Creek Road (approximately 7–10 miles total). Access is via Curtis Creek Campground, Singecat Ridge Overlook (MP 345.5), State Highway 80 (MP 344.1), or the Mt. Mitchell Trailhead. Note that Curtis Creek Road is gated from October 30 to April 1, requiring hikers to walk the road or use Hickory Branch Trail to reach upper trailheads.
Hunting. The area supports white-tailed deer, wild turkey, ruffed grouse, and small game including gray squirrel, fox squirrel, rabbit, raccoon, and opossum under North Carolina's Mountain Zone seasons (deer archery Sept. 6–Oct. 31; gun Nov. 22–Jan. 1; grouse Oct. 13–Feb. 28). Black bear are present in high numbers but protected under the Mackey Mountain Bear Sanctuary designation, where bear hunting is prohibited. The area is part of Pisgah Game Land. Hunters access the interior via Hickory Branch Trail from Curtis Creek Campground or Forest Service roads along the perimeter; the roadless interior requires backcountry navigation through old-growth forest and steep terrain. The absence of roads preserves the remote, undisturbed conditions that support healthy wildlife populations and allow hunters to pursue game in a wild setting.
Fishing. Mackey Creek, a headwater tributary of the Catawba River, supports wild brook trout populations. Hickory Branch, accessed via the Hickory Branch Trail, holds small wild trout. Both streams are classified as Wild Trout Waters under North Carolina regulations: minimum 7-inch length limit, 4-trout daily creel limit, artificial lures with single hooks only. The area is designated Outstanding Resource Water, protecting high water quality critical to native salmonids. Curtis Creek, bordering the eastern boundary, supports brook, brown, and rainbow trout and is part of the state's Hatchery Supported Trout Waters program. Fishing pressure in the interior streams is extremely low due to remoteness and the absence of road access. The roadless condition preserves crystal-clear, cold headwater habitat and ensures that trout streams remain undisturbed by development or fragmentation.
Camping. Curtis Creek Campground and Curtis Creek Roadside Campsites provide developed and dispersed camping near the area's eastern boundary. Black Mountain Campground and Briar Bottom Group Camp are located nearby. These facilities serve as base camps for hikers, hunters, and anglers accessing the roadless interior.
Species with confirmed research-grade observation records from iNaturalist community science data.
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.
Species identified by the U.S. Fish and Wildlife Service as potentially occurring based on range and habitat data.
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.
Composition from LANDFIRE 2024 EVT spatial analysis. Ecosystems classified per NatureServe Terrestrial Ecological Systems.