Recreation & Economy

Quiet, undeveloped recreation on roadless lands supports local economies through tourism, outfitting, hunting, and fishing.

Overview

Roadless areas support a kind of recreation that depends on what isn't there. The Forest Service classifies recreation settings along a spectrum from urban to primitive, and inventoried roadless areas anchor the primitive and semi-primitive end of that spectrum — landscapes where visitors can hike, hunt, fish, camp, and ride in conditions of solitude, quiet, and apparent naturalness. These conditions are not abstract. They are the conditions that hunters seek when they want elk, deer, or bear away from road-accessed crowds; that anglers seek for native trout streams that haven't been warmed or silted by upstream road runoff; that outfitters build small businesses around; and that visitors travel to experience. The recreation roadless areas provide works because access is dispersed, mechanized use is limited, and the landscapes have not been industrialized (USDA Forest Service 2016).

Research on recreation also documents what changes when those conditions break down. Anthropogenic noise — including from vehicle traffic on roads — doubles background sound levels in 63 percent of U.S. protected area units and produces a tenfold increase in 21 percent of them. The same noise affects wildlife: more than 93 percent of studied animal species show measurable responses to recreation disturbance, with the majority of responses being negative. Motorized use in particular brings dust, noise, soil compaction, vegetation damage, and disturbance to cultural resources at scales that non-motorized recreation does not. Forest Service Chief Dale Bosworth named "unmanaged recreation, including impacts from OHVs," as one of four key threats facing national forests in 2004. The kind of recreation roadless areas support is not unlimited or unmanaged; it works because access is constrained (Buxton et al. 2017; Larson et al. 2016; USDA Forest Service 2016).

The economic case for protecting roadless recreation rests on evidence that the "amenity economies" of the rural West increasingly depend on the conditions roadless areas provide. Research on Western U.S. economic growth describes a shift from an "Old West" economy dominated by extractive industries to a "New West" economy in which population, employment, and income growth are driven by environmental amenities, residential appeal, and recreational property. Counties with substantial protected federal lands have shown faster growth in population, employment, and per capita income than counties without — and the growth has been concentrated in service-based industries, including lodging, dining, and professional services (Izon et al. 2010; Holmes & Hecox 2002). The economic value also includes passive use — what economists call the value people place on knowing an area remains intact for future generations. For Western wilderness areas, this value has been estimated at roughly $168 per acre, with wilderness recreation generating an estimated $574 million annually in economic value at an average of $39 per recreation day (Loomis 2000). Rescission would not destroy these values everywhere at once, but it would change the conditions on a substantial share of acreage where they currently exist.

What the research shows

Roadless areas anchor the primitive end of the Forest Service recreation spectrum. Inventoried roadless areas are classified by the agency as supporting primitive and semi-primitive recreation — landscapes characterized by quiet, dispersed access, minimal infrastructure, and apparent naturalness. These conditions are what distinguish backcountry recreation from developed recreation and are not present in roaded areas (USDA Forest Service 2016; USDA Forest Service 2024).

Road noise reaches deep into protected areas. Anthropogenic noise doubles background sound levels in 63 percent of U.S. protected area units and produces a tenfold increase in 21 percent of them. Elevated noise was found in habitats of endangered species, with 14 percent of critical habitats experiencing a tenfold sound increase. Noise pollution in protected areas is closely linked with transportation, development, and extractive land use (Buxton et al. 2017).

Recreation disturbance has measurable effects on wildlife. A systematic review of 274 studies found that more than 93 percent documented at least one effect of non-consumptive recreation on animals, with 59 percent of those effects classified as negative. Motorized use covers larger spatial extents than non-motorized activities and brings additional disturbance through dust, soil compaction, and vegetation damage. Forest Service leadership has named unmanaged recreation as one of four key threats to national forests (Larson et al. 2016; USDA Forest Service 2016).

Western counties with protected federal lands have grown faster. Research on Western U.S. economies describes a shift from an "Old West" economy dominated by extractive industries to a "New West" economy in which growth is driven by environmental amenities and recreational property. Counties with substantial protected federal lands have shown faster growth in population, employment, and per capita income than counties without, with growth concentrated in lodging, dining, and professional services (Izon et al. 2010; Holmes & Hecox 2002).

Wilderness recreation and passive-use values are economically substantial. Economists estimate Western wilderness areas hold passive-use value — the value people place on knowing an area remains intact — at roughly $168 per acre. Wilderness recreation alone generates an estimated $574 million annually in economic value, based on an average of $39 per recreation day. Road construction in roadless areas would not destroy these values everywhere at once, but it would change the conditions on a substantial share of acreage where they currently exist (Loomis 2000; Izon et al. 2010).

Sources

Show all 11 sources

Peer-reviewed research

  1. Izon, G. M., Hand, M. S., Fontenla, M., & Berrens, R. P. (2010). The Economic Value of Protecting Inventoried Roadless Areas: A Spatial Hedonic Price Study in New Mexico. Contemporary Economic Policy, 28(4), 537–553.
  2. Buxton, R. T., McKenna, M. F., Mennitt, D., et al. (2017). Noise pollution is pervasive in U.S. protected areas. Science, 356(6337), 531–533.
  3. Larson, C. L., Reed, S. E., Merenlender, A. M., & Crooks, K. R. (2016). Effects of Recreation on Animals Revealed as Widespread through a Global Systematic Review. PLOS ONE, 11(12), e0167259.
  4. Monz, C., D'Antonio, A., Lawson, S., Barber, J., & Newman, P. (2016). The ecological implications of visitor transportation in parks and protected areas: Examples from research in US National Parks. Journal of Transport Geography, 51, 27–35.
  5. Shannon, G., McKenna, M. F., Angeloni, L. M., et al. (2016). A synthesis of two decades of research documenting the effects of noise on wildlife. Biological Reviews, 91(4), 982–1005.
  6. National Forest Roadless Areas: The Battle Rages On. (2006). Wildlife Society Bulletin, 34(5).
  7. Holmes, P. H., & Hecox, W. E. (2002). Does Wilderness Impoverish Rural Regions? International Journal of Wilderness, 10(3), 34–39.
  8. Loomis, J. B. (2000). Economic Values of Wilderness Recreation and Passive Use. University of Montana.
  9. Trombulak, S. C., & Frissell, C. A. (2000). Review of Ecological Effects of Roads on Terrestrial and Aquatic Communities. Conservation Biology, 14(1), 18–30.

Government and technical sources

  1. USDA Forest Service. (2024). Izembek National Wildlife Refuge Land Exchange / Road Corridor Final Environmental Impact Statement, Chapter 4 — Environmental Consequences.
  2. USDA Forest Service. (2016). Smith River National Recreation Area Restoration and Motorized Travel Management Project, Final Environmental Impact Statement.

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