By virtue of their massive numbers, protected area recreationists pose a real and significant threat to the very resource they so cherish. This is particularly true at backcountry attraction sites, campsites, and along trails, where visitation and its effects are concentrated. Specific consequences of visitation to these areas include the trampling and subsequent loss of ground vegetation, shrubs, tree seedlings, and felling of saplings; erosion of surface litter and humus; exposure, erosion, and compaction of mineral soil; and exposure of tree roots and damage to tree trunks.
In the United States, the National Park Service and Forest Service have recognized the need for visitor management and re- source protection programs to balance visitation with its associated resource impacts. The recurring question, "are we loving our parks to death?" increasingly challenges managers to develop and implement management policies, strategies, and actions that permit the recreational use of park and wilderness areas without compromising their ecological and aesthetic integrity.
The discussion that follows presents some of the principal findings and management implications of a relatively new discipline of scientific research: recreation ecology. Scientists in this discipline generally seek to identify the type and extent of resource impacts and to evaluate relationships between use-related, environmental, and managerial factors. The capabilities and managerial values of recreation impact monitoring are also described. This paper is informal, references to scientific literature are included only in a final "Recommended Readings" section.
Studies of visitor impacts to campsites and trails have documented that most resource impacts are related to visitor use levels in a curvilinear fashion. For example, a study of wilderness campsites in Minnesota found that only 12 nights of campsite use per year caused substantial biophysical changes, while further increases in use caused little additional change for most forms of impact (Figure 1). A few impact parameters, such as loss of tree seedlings, are highly affected by very low levels of site use. In contrast, the exposure of mineral soil occurs later in the progression of impacts, and is related to use intensity in a more linear fashion. The majority of impact parameters, such as vegetation loss, are intermediate in their response.
One important implication of the curvilinear use/impact relationship is that nearly all use must be eliminated to achieve significant
reductions in most forms of recreational impact. Level of use is an inherent determinant of recreational impacts but research has
demonstrated the importance of many other factors. Three categories of influential factors and their potential for manipulation by
managers are described: use-related, environmental, and managerial factors. This review is not comprehensive, the aim is to
illustrate the diversity of options available to managers for reducing visitor impacts. Managers are also cautioned to consider
the costs of implementation and costs to the quality of visitor experiences associated with alternative actions.
Use-Related Factors
Managers are often able to control or influence a number of use-related factors shown by research to be important determinants of recreational impacts. As noted, the curvilinear use/impact relationship implies that managers would have to reduce or disperse use to extremely low levels to achieve significant reductions in most types of impacts. Research has also shown that some types of use (e.g., horse or off-road vehicle use) are more impacting, on a per capita basis, than others ( e.g., hiking). Managers can prohibit such uses or restrict them to resistant environments or sites specifically designed and maintained to accommodate their higher impacts.
Many impacts are the result of uninformed or careless behavior. Managers can educate and regulate visitors to reduce high- impact behavior (e.g., building fires, chopping on trees, cutting switchbacks) and encourage low-impact behavior. Finally, large groups have a greater potential to damage resources than the same number of individuals in smaller groups. Limits on group sizes are often encouraged or required to minimize resource impacts.
Environmental Factors
Through their control over the selection of recreation sites and layout of trails, managers have the ability to minimize resource impacts by encouraging recreational use in impact resistant locations. For example, research has demonstrated considerable variability in the trampling resistance of different vegetative growth forms. In the Boundary Waters Canoe Area, vegetation groundcover averaged 52% on campsites with less than 25% tree cover, but only 4% on campsites with 75-100% tree cover. Campsites with greater sunlight penetration supported shade-intolerant grasses and sedges which, due to their flexible growth forms and other unique characteristics, are significantly more resistant to trampling than most broad-leafed herbaceous plants. The resistance of vegetation to trampling also varies by season of year. Vegetation is more susceptible to damage during the growing season and whenever soils are wet.
Similarly, soils vary in their susceptibility to compaction, as influenced by texture, organic content, and moisture. Soils with a wide range of particle sizes (e.g., loams), low organic content, and moderate to high moisture level are the most prone to compaction. Soils most prone to erosion are those with a narrow range of particle sizes, particularly those high in silt and fine sands. Both soil compaction and erosion are accelerated by the absence of vegetation and litter cover and slope is a critical factor influencing soil erosion.
Knowledge of the relative resiliency (ability to recover) of different vegetation and soil types can be used to select areas
which will quickly recover following recreational trampling. Vegetation resiliency is primarily related to the length of
growing season and soil productivity. Sites with high resiliency are also desirable because they support dense vegetation
which helps confine use to campsites and trails. Soil resiliency is related to soil texture, soil moisture, freeze and thaw cycles,
and biological activity in the soil. Recreation ecology research has shown that recovery rates on campsites and trails are
considerably lower than initial impact rates, indicating that rest-rotation schemes will generally be ineffective (Figure 2).
Managerial Factors
Visitor and site management techniques comprise the final group of factors available to managers for minimizing recreation impacts. The curvilinear use/impact relationship limits the effectiveness of use limitation as a management action. Managers of some protected areas have sought to minimize impacts by encouraging visitor dispersal. However, due to the use/impact relationship and a number of behavioral factors, this impact-minimization strategy has been successful only in areas which receive low use. Most visitors prefer hiking on established trails and camping on existing campsites. Many visitors enjoy camping close to trails and other groups for social reasons, others fear getting lost when away from trails. Areas with mountainous terrain and/or dense vegetation may limit the ability of visitors to hike off-trail or the number of suitable camping locations necessary to support a dispersed camping policy. Pre-existing trails and campsites are also more convenient, comfortable, and require less work to use. Finally, water and other scenic attractions in the backcountry will always attract larger numbers of visitors than less interesting areas. In general, management efforts to alter these natural tendencies will be unsuccessful without substantial and prohibitively expensive educational and law enforcement programs.
The opposite of dispersal, visitor containment or concentration, offers a more promising strategy for minimizing recreation impacts. Trails, which concentrate use on their treads, represent one form of containment. Furthermore, formal trails can be routed to take advantage of resistant and resilient environments while avoiding sensitive locations. Similarly, designated campsites also contain visitors and can be specifically located to minimize resource impacts.
Figure 3 illustrates the curvilinear use/impact curve and these two impact minimization strategies for
campsites. To the right of the curves' inflection point, use levels on individual campsites can be increased two- and
three-fold with comparatively small increases in impact. Impact is minimized not only by containing use on and within
campsites but also by limiting the number of campsites to the smallest number necessary to accommodate a given amount
of use. Use can also be contained by encouraging or requiring visitors to use existing (but not designated) campsites.
These strategies can also be effectively combined, for example, requiring visitors to use designated sites in high use areas,
existing user-selected sites in moderate use areas, and dispersed camping in lightly used areas. Such a policy would require
a permit system to convey this complexity but protects resources as well as visitor freedom to travel and camp where they choose.
Area closures represent the most restrictive policy for preventing visitor impacts. The closure of specific areas to trails and/or camping is justified when sensitive or rare species and habitats must be protected. They may also be appropriate when their effect is to shift use from impact-susceptible locations to impact-resistant locations. However, managers have often used areas closures to remedy situations where impacts have simply reached unacceptable levels. Unless additional measures are implemented to prevent a reoccurrence of the impacts, an area closure has the short-term effect of resolving the problems only to have them reoccur in new locations at a later date.
Finally, site selection, construction, maintenance, and rehabilitation programs offer great potential for minimizing resource impacts. For example, trail construction and maintenance practices have long been used by managers to promote good trail drainage and to harden trail treads to sustain trampling pressures. Trail location and maintenance may well be more critical than type and amount of use in influencing soil erosion, perhaps the most significant form of trail impact. These types of site management programs are less commonly applied to recreation sites or campsites but offer the same potential to minimize impacts. Such practices can be applied to select and prepare sites to resist deterioration under use, to minimize many types of site impacts (e.g., site expansion), and to speed recovery on recreation sites damaged by use.
Visitor impact monitoring programs provide an objective record of resource conditions, even though individual managers may
come and go. The type, magnitude, and, in some instances, the causes of resource deterioration and improvement can be
detected and evaluated. Deteriorating conditions can be detected before severe or irreversible impacts occur, allowing time
for implementing corrective actions. Relationships between specific impacts and other controlling factors may suggest effective
management actions. Monitoring data also permits an evaluation of the success or failure of implemented resource protection
measures.
Finally, a visitor impact monitoring program provides an essential element for recreation resource planning and management frameworks such as the Limits of Acceptable Change (LAC) or Visitor Impact Management (VIM) systems (Figure 4). These frameworks evolved from and are currently replacing management approaches based on the more traditional carrying capacity model.
Under the LAC and VIM frameworks, numerical standards can be set for individual impact parameters to specify the limits of acceptable change. These limits define the critical boundary line between acceptable and unacceptable conditions, establishing a measurable reference point to which future conditions can be compared. A visitor impact monitoring program can provide information necessary for formulating realistic standards and for periodically evaluating resource conditions in relation to these standards.
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Keller, Kit. 1990. Mountain Bikes on Public Lands: A Manager's Guide to the State of the Practice. Bicycle Federation of America, Inc.. Washington, D.C. 68 pp.
Proudman, Robert D. and Reuben Rajala. 1981. Trail Building and Maintenance. 2nd ed., Appalachian Mountain Club, Boston, MA, 286 pp.
Cole, David N. 1983. Monitoring the Condition of Wilderness Campsites. U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. Research Paper INT-302. Ogden, Utah. 10 pp.
Cole, David N. 1989. Wilderness Campsite Monitoring Methods: A Sourcebook. U.S. Department of Agriculture, Forest Service, Intermountain Forest Experiment Station. General Technical Rpt. INT-259. Ogden, Utah. 57 pp.
Marion, Jeffrey L. 1991. Developing a Natural Resource Inventory and Monitoring Program for Visitor Impacts on Recreation Sites: A Procedural Manual. U.S. Department of Interior, National Park Service, Natural Resources Report NPS/NRVT/NRR-91/06, 59 pp.
Manning, Robert E., David W. Lime, and Wayne A. Freimund. 1995. The Visitor Experience and Resource Protection (VERP) process: The application of carrying capacity to Arches National Park. The George Wright FORUM 12(3):41- 55.
Stankey, George H., David N. Cole, Robert C. Lucas, Margaret E. Petersen, and Sidney S. Frissell. 1985. The Limits of Acceptable Change (LAC) System for Wilderness Planning. U.S. Department of Agriculture, Forest Service, Inter- mountain Forest Experiment Station. General Technical Report INT-176. Ogden, Utah. 37 pp.
Marion, Jeffrey L. and Toivo Sober. 1987. Environmental impact management in the Boundary Waters Canoe Area Wilderness. Northern Journal of Applied Forestry 4(1):7-10.
Hendee, John C., George H. Stankey, and Robert C. Lucas. 1990. Wilderness Management. North American Press: Golden, CO. 546 pp.
Marion, Jeffrey L., Joseph W. Roggenbuck, and Robert E. Manning. 1993. Problems and Practices in Backcountry Recreation Management: A Survey of National Park Service Managers. U.S. Department of Interior, National Park Service, Natural Resources Report NPS/NRVT/NRR-93/12, 63 p.
Cole, David N. and Jim Benedict. 1983. Wilderness campsite selection: What should users be told. Park Science 3(4):5-7.
Cole, David N. 1989. Low-Impact Recreational Practices for Wilderness and Backcountry. U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Expt. Stn. General Technical Report INT-265. Ogden, UT. 131 pp.
Hampton, Bruce and David N. Cole. 1995. Soft Paths: How to Enjoy the Wilderness Without Harming It. Stackpole Books: Mechanicsburg, PA. 222 pp.
Leave No Trace Skills & Ethics Series. Pamphlets, booklets, and other materials available from the National Outdoor Leadership School as part of a cooperative program with the U.S. federal wilderness management agencies. Information is both generic and specific to different geographic regions, recreation environments, and uses. Call 1-800-332-4100. Website: http://www.lnt.org/