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42<br />

Journal <strong>of</strong> Park <strong>and</strong> Recreation Adm<strong>in</strong>istration<br />

Fall 2010<br />

Volume 28, Number 3<br />

pp. 42-60<br />

<strong>GPS</strong>-<strong>Based</strong> <strong>Measurements</strong> <strong>of</strong><br />

<strong>Backcountry</strong> <strong>Visitors</strong> <strong>in</strong> <strong>Parks</strong> <strong>and</strong><br />

Protected Areas: Examples <strong>of</strong><br />

Methods <strong>and</strong> Applications from<br />

Three Case Studies<br />

Ashley D’Antonio<br />

Christopher Monz<br />

Steve Lawson<br />

Peter Newman<br />

Dave Pettebone<br />

Alyson Courtemanch<br />

EXECUTIVE SUMMARY: Underst<strong>and</strong><strong>in</strong>g the spatial pattern <strong>of</strong> visitor use <strong>in</strong> parks<br />

is essential for protect<strong>in</strong>g park resources <strong>and</strong> visitor experiences. Information<br />

on the specific locations <strong>and</strong> <strong>in</strong>tensity <strong>of</strong> use can provide an important “early<br />

warn<strong>in</strong>g” <strong>of</strong> locations <strong>of</strong> potential visitor resource impact <strong>and</strong> <strong>of</strong> times <strong>and</strong> places<br />

where visitor density is suggestive <strong>of</strong> crowd<strong>in</strong>g <strong>and</strong> other experience issues. Past<br />

studies have traditionally used techniques such as automated visitor counters,<br />

observational methodologies, <strong>and</strong> survey techniques to ga<strong>in</strong> an underst<strong>and</strong><strong>in</strong>g <strong>of</strong><br />

the spatial component <strong>of</strong> visitor use behavior <strong>and</strong> <strong>of</strong> visitor use <strong>in</strong>tensity. However,<br />

these methods have various limitations <strong>in</strong>clud<strong>in</strong>g logistical considerations <strong>and</strong><br />

the reliability <strong>and</strong> accuracy <strong>of</strong> the techniques. This research reports on recent<br />

methodological advances <strong>in</strong> three studies where global position<strong>in</strong>g system (<strong>GPS</strong>)<br />

track<strong>in</strong>g methodologies was used to determ<strong>in</strong>e the locations <strong>and</strong> densities <strong>of</strong><br />

visitor use along trail corridors. <strong>GPS</strong>-based methods were used <strong>in</strong> the Tuolumne<br />

Meadows trail system <strong>of</strong> Yosemite National Park to underst<strong>and</strong> visitor use at this<br />

popular hik<strong>in</strong>g dest<strong>in</strong>ation, with<strong>in</strong> the Bear Lake Corridor <strong>of</strong> Rocky Mounta<strong>in</strong><br />

National Park to exam<strong>in</strong>e the spatial patterns <strong>of</strong> visitor use, <strong>and</strong> <strong>in</strong> the Teton<br />

Range to measure the frequency, tim<strong>in</strong>g, <strong>and</strong> <strong>in</strong>tensity <strong>of</strong> w<strong>in</strong>ter backcountry<br />

recreation. F<strong>in</strong>d<strong>in</strong>gs from these studies suggest that <strong>GPS</strong> track<strong>in</strong>g methodology<br />

holds significant promise. <strong>GPS</strong>-based methods can be used to gather both spatial<br />

<strong>and</strong> temporal <strong>in</strong>formation about visitors <strong>in</strong> a variety <strong>of</strong> protected area management<br />

situations. The data result<strong>in</strong>g from <strong>GPS</strong> strategies are ample, detailed, <strong>and</strong><br />

more accurate spatially than data collected us<strong>in</strong>g traditional methodologies.<br />

<strong>GPS</strong> track<strong>in</strong>g methodology has the potential to be comb<strong>in</strong>ed with other data<br />

sources, such as visitor surveys <strong>and</strong> recreation ecology assessments, to provide<br />

an important use-related context to these approaches. Overall, <strong>GPS</strong> track<strong>in</strong>g can<br />

be used to ga<strong>in</strong> <strong>in</strong>formation vital to the underst<strong>and</strong><strong>in</strong>g <strong>of</strong> several contemporary


issues <strong>in</strong> protected area management such as visitor experience <strong>and</strong> natural<br />

resource impacts, visitor-wildlife concerns, <strong>and</strong> visitor soundscape experiences.<br />

KEYWORDS: Global position<strong>in</strong>g system, visitor use patterns, visitor behavior,<br />

visitor use estimation, recreation management<br />

AUTHORS: Ashley D’Antonio is with the Department <strong>of</strong> Environment <strong>and</strong> Society,<br />

Utah State University, 5215 Old Ma<strong>in</strong> Hill, Logan, UT 84322, phone: (435)<br />

797-1009, email: ashleydantonio@gmail.com. Monz is with the Department<br />

<strong>of</strong> Environment <strong>and</strong> Society, Ecology Center, Utah State University. Lawson is<br />

with the Resource Systems Group, Inc, Burl<strong>in</strong>gton, Vermont. Newman is with<br />

the Department <strong>of</strong> Human Dimensions <strong>of</strong> Natural Resources, Colorado State<br />

University. Pettebone is with the National Park Service at Yosemite National<br />

Park. Courtemanch is with the Department <strong>of</strong> Zoology & Physiology, University<br />

<strong>of</strong> Wyom<strong>in</strong>g<br />

ACKNOWLEDGMENTS: The authors thank Karen Hockett, Logan Park, Derrick<br />

Taff, <strong>and</strong> Larry Gamble for considerable help with the design <strong>and</strong> development <strong>of</strong><br />

this study. This work was supported by grants from the Alternative Transportation<br />

<strong>in</strong> <strong>Parks</strong> <strong>and</strong> Public L<strong>and</strong>s Program adm<strong>in</strong>istered through the National Park<br />

Service <strong>and</strong> the S.J. <strong>and</strong> Jessie E. Qu<strong>in</strong>ney Foundation. The second author also<br />

thanks the Utah State Agricultural Experimentation for fund<strong>in</strong>g support dur<strong>in</strong>g<br />

several phases <strong>of</strong> this work.<br />

Participation <strong>in</strong> outdoor recreation <strong>and</strong> visitation to parks <strong>and</strong> protected areas<br />

has <strong>in</strong>creased over recent decades <strong>in</strong> the United States (Cordell, 2008) <strong>and</strong> worldwide<br />

(De Lacy & Whitmore, 2006). As the number <strong>of</strong> visitors to parks <strong>and</strong> protected areas<br />

<strong>in</strong>creases, there is potential for the expansion <strong>and</strong> proliferation <strong>of</strong> recreation resource<br />

impact <strong>and</strong> dim<strong>in</strong>ished visitor experience (Hammit & Cole, 1998; Mann<strong>in</strong>g, 1999). From<br />

a resource perspective, the extent <strong>of</strong> impact is <strong>in</strong>fluenced by the type, amount, location,<br />

<strong>and</strong> spatial <strong>and</strong> temporal distribution <strong>of</strong> visitor use (Hammit & Cole, 1998; Newsome,<br />

Moore, & Dowl<strong>in</strong>g, 2002; Monz, Cole, Marion, & Leung, 2010). As such, managers<br />

<strong>of</strong>ten f<strong>in</strong>d it useful to underst<strong>and</strong> several attributes <strong>of</strong> visitor use <strong>in</strong>clud<strong>in</strong>g the number<br />

<strong>of</strong> visitors <strong>in</strong> an area or system, spatial patterns <strong>of</strong> visitor use, <strong>and</strong> visitor behavior as<br />

possible “early warn<strong>in</strong>gs” <strong>of</strong> resource change. Similar strategies can be employed from a<br />

visitor experience perspective, as underst<strong>and</strong><strong>in</strong>g use is suggestive <strong>of</strong> issues <strong>of</strong> crowd<strong>in</strong>g<br />

<strong>and</strong> dim<strong>in</strong>ished visitor experiences. Managers can also utilize <strong>in</strong>formation related to visitor<br />

use to better underst<strong>and</strong> the relationship between impact <strong>and</strong> use, underst<strong>and</strong> trends, assign<br />

priorities for management action <strong>and</strong> facility development, <strong>and</strong> as <strong>in</strong>put for statistical <strong>and</strong><br />

simulation models <strong>of</strong> visitor use (Lawson, 2006; Leonard, Echelberger, Plumley, & Van<br />

Meter, 1980). A thorough underst<strong>and</strong><strong>in</strong>g <strong>of</strong> visitor use levels <strong>and</strong> patterns can contribute to<br />

a more complete underst<strong>and</strong><strong>in</strong>g <strong>of</strong> many important issues <strong>in</strong> protected area management<br />

<strong>in</strong>volv<strong>in</strong>g visitor experience <strong>and</strong> resource protection priorities.<br />

Past research exam<strong>in</strong><strong>in</strong>g visitor use has focused primarily on estimat<strong>in</strong>g use levels.<br />

Developed approaches can be categorized as self-count<strong>in</strong>g methods, direct-count methods,<br />

<strong>and</strong> <strong>in</strong>direct-count methods (Hollenhorst, Whisman, & Ewert, 1992; Watson, Cole, Turner,<br />

& Reynolds, 2000). The earliest count<strong>in</strong>g techniques used by managers <strong>of</strong> parks <strong>and</strong><br />

protected areas were self-count<strong>in</strong>g techniques such as voluntary registration, self-issued<br />

43


44<br />

permits, <strong>and</strong>, <strong>in</strong> some locations, m<strong>and</strong>atory permits (Wenger & Gregerson, 1964; Wagar,<br />

1969; James, 1971; Hendee & Lucas, 1973; Hollenhorst et al., 1992). However, selfcount<strong>in</strong>g<br />

techniques are subject to <strong>in</strong>accuracies due to noncompliance by visitors <strong>and</strong>, <strong>in</strong><br />

order to accurately estimate use, managers must make adjustments for noncompliance <strong>and</strong><br />

calibrate accord<strong>in</strong>gly (Thorsell, 1967; Echelberger, Leonard, & Plumley, 1981; Leatherberry<br />

& Lime, 1981). Self-registration <strong>and</strong> self-issued or m<strong>and</strong>atory permits are <strong>of</strong>ten best used<br />

<strong>in</strong> areas where access to l<strong>and</strong>s is restricted (Muhar, Arnberger, & Br<strong>and</strong>enburg, 2000). The<br />

<strong>in</strong>formation collected from self-count<strong>in</strong>g techniques is useful but <strong>of</strong>ten lacks descriptive<br />

<strong>in</strong>formation such as visitor use patterns, visitor characteristics, motivations, <strong>and</strong> behavior.<br />

Direct count<strong>in</strong>g methods such as observational techniques <strong>and</strong> surveys can provide<br />

managers with use estimations as well as more detailed <strong>in</strong>formation related to visitor use<br />

patterns <strong>and</strong> behavior. Observational techniques, whether roam<strong>in</strong>g or stationary, have<br />

the advantage <strong>of</strong> be<strong>in</strong>g unobtrusive <strong>and</strong> dem<strong>and</strong> no time on visitors (Schreuder, Tyre, &<br />

James, 1975; Hollenhorst et al., 1992; Schaick & van der Spek, 2008). However, these<br />

methodologies are time consum<strong>in</strong>g for staff <strong>and</strong> are subject to a variety <strong>of</strong> accuracy issues<br />

(Arnberger, Haider, & Br<strong>and</strong>enburg, 2005). Observational data are frequently dependent<br />

on the tra<strong>in</strong><strong>in</strong>g <strong>of</strong> a large team <strong>of</strong> technicians, <strong>and</strong> the accuracy <strong>of</strong> results relies on <strong>in</strong>terobserver<br />

reliability (Park, Mann<strong>in</strong>g, Marion, Lawson, & Jacobi, 2008). Observational<br />

studies provide visual <strong>in</strong>terpretations <strong>of</strong> visitor behavior <strong>and</strong> thus lack non-visual<br />

demographical data <strong>and</strong> detailed <strong>in</strong>formation related to visitor it<strong>in</strong>eraries or motivations<br />

(Shoval & Issacson, 2007).<br />

Survey techniques, however, can provide some <strong>of</strong> this lack<strong>in</strong>g <strong>in</strong>formation regard<strong>in</strong>g<br />

visitor use patterns, demographics, detailed it<strong>in</strong>eraries, <strong>and</strong> visitor motivations (James &<br />

Harper, 1965; Kovacs, 1970). Surveys are particularly useful <strong>in</strong> situations <strong>of</strong> dispersed<br />

visitor use where observational techniques may not be feasible (Cushwa & McG<strong>in</strong>nes,<br />

1963; James & Henley 1968; Hollenhorst et al., 1992). However, survey methodology<br />

dem<strong>and</strong>s a significant time <strong>in</strong>vestment from visitors <strong>and</strong> is susceptible to issues <strong>of</strong> accuracy<br />

(Hallo, Mann<strong>in</strong>g, Valliere, & Budruk, 2005). Often surveys exam<strong>in</strong><strong>in</strong>g visitor use patterns<br />

will require participants to recall characteristics <strong>of</strong> their visit, <strong>in</strong>troduc<strong>in</strong>g opportunities<br />

for <strong>in</strong>accuracies <strong>and</strong> biased results (Park et al., 2008). Visitor diaries may reduce issues <strong>of</strong><br />

recall bias but require an even higher dem<strong>and</strong> on visitor time than other survey techniques<br />

(Shoval & Isaacson, 2007). F<strong>in</strong>ally, the data entry <strong>and</strong> analysis result<strong>in</strong>g from survey-based<br />

studies can be extremely time consum<strong>in</strong>g <strong>and</strong> tedious (Hallo et al., 2005).<br />

As automated technology for count<strong>in</strong>g visitors became available <strong>in</strong> the late 1960s,<br />

<strong>in</strong>direct-count<strong>in</strong>g techniques became widely used <strong>in</strong> parks <strong>and</strong> protected areas to estimate<br />

visitor use levels. Indirect-count<strong>in</strong>g techniques <strong>in</strong>clude pressure plates, automatic trail<br />

counters us<strong>in</strong>g photoelectric technology, <strong>and</strong> electronic vehicle counters (James & Ripley,<br />

1963; Leonard et al., 1980; Hollenhorst et al., 1992). The use <strong>of</strong> automated counters is<br />

commonplace as they are relatively <strong>in</strong>expensive <strong>and</strong> easy to set up <strong>and</strong> ma<strong>in</strong>ta<strong>in</strong> (Watson<br />

et al., 2000). Recent technological advances <strong>in</strong> dual <strong>and</strong> array passive <strong>in</strong>frared technology<br />

have allowed automatic trail counters to collect <strong>in</strong>formation related to visitor use patterns,<br />

such as speed <strong>and</strong> direction, as well as use estimates. However, these counters are<br />

expensive <strong>and</strong> can be sensitive to temperature changes <strong>in</strong> the environment (Greene-Roesel,<br />

Diogenes, Ragl<strong>and</strong>, & L<strong>in</strong>dau, 2008). While the data from counters are clearly useful,<br />

even with technological advances, counters alone cannot provide specifics such as visitor<br />

demographics or specific visitor it<strong>in</strong>eraries (Arrowsmith & Chhetri, 2003; O’Connor,<br />

Zerger, & Itami, 2005). Visitor counter methodology is also subject to confound<strong>in</strong>g factors<br />

such as accuracy, calibration, <strong>and</strong> battery life (Pettebone, 2009).<br />

In order for managers to make the most <strong>in</strong>formed management actions, detailed,<br />

specific <strong>in</strong>formation about both visitor use <strong>in</strong>tensity <strong>and</strong> patterns is required. Moreover,


many contemporary issues <strong>in</strong> protected area management are more thoroughly understood<br />

with a detailed exam<strong>in</strong>ation <strong>of</strong> visitor use patterns. Although self-count<strong>in</strong>g, directcount<strong>in</strong>g,<br />

<strong>and</strong> <strong>in</strong>direct-count<strong>in</strong>g approaches can provide useful <strong>in</strong>formation to managers,<br />

research us<strong>in</strong>g global position<strong>in</strong>g system (<strong>GPS</strong>) technology has shown significant promise<br />

<strong>in</strong> provid<strong>in</strong>g more detailed data from which to exam<strong>in</strong>e visitor use patterns <strong>and</strong> <strong>in</strong>tensity,<br />

as well as visitor flows <strong>and</strong> densities (Hallo et al., 2005; O’Connor et al., 2000). Recent<br />

studies have used <strong>GPS</strong> track<strong>in</strong>g methodologies to collect <strong>in</strong>formation on the spatial extent,<br />

patterns, <strong>and</strong> <strong>in</strong>tensity <strong>of</strong> visitor use (Lai, Li, Chan, & Kwong, 2007; Ligtenburg, van<br />

Marwijk, Moelans, & Kuijpers, 2008). These studies <strong>in</strong>dicate that the <strong>in</strong>formation collected<br />

us<strong>in</strong>g <strong>GPS</strong>-based technology is more accurate, more detailed, <strong>and</strong> more robust than data<br />

collected from traditional methodologies (Hallo et al., 2005). Compared to observational<br />

<strong>and</strong> survey techniques, <strong>GPS</strong>-based methodologies require m<strong>in</strong>imal time dem<strong>and</strong>s on the<br />

visitor <strong>and</strong> less tra<strong>in</strong><strong>in</strong>g <strong>of</strong> staff for data collection (Hallo et al., 2005).<br />

<strong>GPS</strong>-based approaches can also provide data that has been heret<strong>of</strong>ore difficult to<br />

collect. First, <strong>in</strong> many protected area situations, visitors depart<strong>in</strong>g from designated trails<br />

<strong>and</strong> sites are <strong>of</strong> <strong>in</strong>creas<strong>in</strong>g management concern. Short <strong>of</strong> observational studies, no<br />

techniques are readily available to determ<strong>in</strong>e the spatial extent <strong>and</strong> duration <strong>of</strong> <strong>of</strong>f-trail<br />

use. <strong>GPS</strong>-based measurements provide results with enough detail to exam<strong>in</strong>e relatively<br />

small-scale visitor movements both on <strong>and</strong> <strong>of</strong>f-trail. Second, precise <strong>in</strong>formation about<br />

visitor use levels <strong>and</strong> patterns is helpful <strong>in</strong> develop<strong>in</strong>g <strong>and</strong> validat<strong>in</strong>g computer models that<br />

are becom<strong>in</strong>g a more common tool to identify visitor flows <strong>in</strong> parks <strong>and</strong> protected areas<br />

(e.g., Lawson, 2006). These data have traditionally been measured via survey methods,<br />

which have limited spatial <strong>and</strong> temporal precision due to recall bias <strong>and</strong> limits to visitors’<br />

knowledge <strong>of</strong> areas studied. <strong>GPS</strong> approaches can be used to collect model<strong>in</strong>g <strong>in</strong>puts <strong>and</strong><br />

have the potential to be more reliable <strong>and</strong> accurate data sources.<br />

This study reports on the development <strong>of</strong> <strong>GPS</strong>-based measurements <strong>of</strong> visitor<br />

use patterns through the exam<strong>in</strong>ation <strong>of</strong> three case studies that utilized <strong>GPS</strong> track<strong>in</strong>g<br />

methodologies; a visitor track<strong>in</strong>g study <strong>in</strong> Yosemite National Park, a day-use visitor<br />

track<strong>in</strong>g study <strong>in</strong> the Bear Lake Corridor <strong>of</strong> Rocky Mounta<strong>in</strong> National Park, <strong>and</strong> a w<strong>in</strong>ter<br />

recreation study <strong>in</strong> the Teton Range <strong>of</strong> Wyom<strong>in</strong>g. In the course <strong>of</strong> these <strong>in</strong>vestigations, we<br />

conducted extensive track<strong>in</strong>g <strong>of</strong> visitors via r<strong>and</strong>om sampl<strong>in</strong>g at trailheads <strong>in</strong> each study<br />

area <strong>and</strong> developed accuracy-check<strong>in</strong>g procedures to m<strong>in</strong>imize positional errors associated<br />

with the current, available <strong>GPS</strong> technology. Our goal <strong>in</strong> this paper is to illustrate the utility<br />

<strong>of</strong> <strong>GPS</strong> track<strong>in</strong>g as a means <strong>of</strong> ga<strong>in</strong><strong>in</strong>g further underst<strong>and</strong><strong>in</strong>g <strong>of</strong> several important protected<br />

area management issues.<br />

Method<br />

Study Areas<br />

Yosemite National Park. Yosemite National Park (YNP) is located <strong>in</strong> the Sierra<br />

Nevada range <strong>of</strong> California approximately 240 km east <strong>of</strong> the San Francisco Bay area. As<br />

one <strong>of</strong> the most visited parks <strong>in</strong> the United States, YNP receives over 3.5 million visitors<br />

annually (National Park Service, 2009). While the majority <strong>of</strong> park use is concentrated <strong>in</strong><br />

Yosemite Valley, the Tuolumne Meadows area <strong>of</strong> the park <strong>of</strong>fers visitors opportunities for<br />

day hik<strong>in</strong>g, backpack<strong>in</strong>g, rock climb<strong>in</strong>g, <strong>and</strong> fish<strong>in</strong>g <strong>in</strong> an alp<strong>in</strong>e environment. Trailheads<br />

<strong>in</strong> the Tuolumne Meadows area <strong>of</strong> the park provide access to vast areas <strong>of</strong> congressionally<br />

designated Wilderness <strong>and</strong> are accessed via Tioga Road, which is a National Scenic Byway.<br />

The National Park Service is conduct<strong>in</strong>g transportation <strong>and</strong> visitor use plann<strong>in</strong>g<br />

activities throughout the park, <strong>in</strong>clud<strong>in</strong>g collect<strong>in</strong>g <strong>in</strong>formation to underst<strong>and</strong> relationships<br />

among vehicle traffic volumes, visitor use levels <strong>in</strong> locations throughout the park, the<br />

45


46<br />

quality <strong>of</strong> visitors’ experiences, <strong>and</strong> park resource conditions. To support park plann<strong>in</strong>g,<br />

<strong>GPS</strong>-based track<strong>in</strong>g data were collected dur<strong>in</strong>g summer 2009 to measure visitor use<br />

patterns <strong>in</strong> Tuolumne. Specifically, research technicians were stationed at five trailheads<br />

along Tioga Road <strong>and</strong> recruited visitor groups to participate <strong>in</strong> the study (see Figure 1).<br />

In addition, <strong>in</strong>frared trail counters were <strong>in</strong>stalled at each <strong>of</strong> the five trailhead locations to<br />

measure daily trailhead visitation.<br />

Rocky Mounta<strong>in</strong> National Park. Rocky Mounta<strong>in</strong> National Park (RMNP) is located<br />

<strong>in</strong> north central Colorado, approximately 160 km from the Denver metropolitan area.<br />

RMNP receives over 3 million visitors per year (National Park Service, 2009). One <strong>of</strong> the<br />

most popular dest<strong>in</strong>ations with<strong>in</strong> RMNP is the Bear Lake Road Corridor, which provides<br />

access to many alp<strong>in</strong>e lakes <strong>and</strong> is a popular dest<strong>in</strong>ation for day users, backpackers, <strong>and</strong><br />

boulderers. In 1998, due to the high level <strong>of</strong> use <strong>in</strong> the Bear Lake Road Corridor, RMNP<br />

created a shuttle bus system to service the area (Gamble, Lawson, Monz, & Newman, 2007).<br />

Ridership on the shuttle bus to the Bear Lake Road Corridor has <strong>in</strong>creased substantially<br />

s<strong>in</strong>ce its <strong>in</strong>stallment, result<strong>in</strong>g <strong>in</strong> apparent <strong>in</strong>creased visitation to hik<strong>in</strong>g dest<strong>in</strong>ations <strong>in</strong> this<br />

corridor.<br />

<strong>GPS</strong>-based track<strong>in</strong>g methodologies were performed at three trailheads served by the<br />

shuttle bus <strong>in</strong> the Bear Lake Road Corridor; Bear Lake, Glacier Gorge, <strong>and</strong> Bierstadt Lake.<br />

Participants <strong>in</strong> the study were asked to complete an optional survey at the end <strong>of</strong> their hike<br />

that gathered <strong>in</strong>formation on crowd<strong>in</strong>g <strong>and</strong> visitor behavior <strong>in</strong> response to crowd<strong>in</strong>g.<br />

The Teton Range. Gr<strong>and</strong> Teton National Park (GTNP) receives 2.5 million visitors<br />

annually <strong>and</strong> is located <strong>in</strong> Northwestern Wyom<strong>in</strong>g bordered by Yellowstone National Park<br />

<strong>and</strong> two National Forest Service units. To the east <strong>and</strong> south <strong>of</strong> GTNP is the Bridger-Teton<br />

National Forest (BTNF) <strong>and</strong> to the west <strong>of</strong> GTNP is the Caribou-Targhee National Forest<br />

(CTNF).<br />

The Teton Range supports the smallest native bighorn sheep population <strong>in</strong> Wyom<strong>in</strong>g.<br />

Due to anthropogenic disturbance at lower elevations, the Teton Range bighorn sheep<br />

(Ovis canadensis) herd resides year-round at high elevation <strong>in</strong> the Teton Range (Kauffman<br />

& Courtemanch, 2009). Although nearly all <strong>of</strong> the bighorn sheep w<strong>in</strong>ter range falls<br />

with<strong>in</strong> designated Wilderness, where motorized recreation is prohibited, non-motorized<br />

recreation such as backcountry ski<strong>in</strong>g is popular. Participation <strong>in</strong> backcountry ski<strong>in</strong>g is<br />

rapidly <strong>in</strong>creas<strong>in</strong>g <strong>in</strong> the Teton Range <strong>and</strong> has the potential to <strong>in</strong>fluence bighorn sheep<br />

w<strong>in</strong>ter habitat use patterns (Kauffman & Courtemanch, 2009).<br />

Trail counter <strong>and</strong> <strong>GPS</strong>-based track<strong>in</strong>g data were collected at seven popular<br />

backcountry access po<strong>in</strong>ts <strong>in</strong> the Teton Range from January to April <strong>of</strong> the 2009 w<strong>in</strong>ter<br />

recreation season. These access po<strong>in</strong>ts <strong>in</strong>cluded three backcountry gates at Jackson Hole<br />

Mounta<strong>in</strong> Resort (where skiers enter BTNF <strong>and</strong> GNTP), Death Canyon trailhead <strong>in</strong> GTNP,<br />

Bradley-Taggart Lake trailhead <strong>in</strong> GTNP, <strong>and</strong> Teton Canyon <strong>and</strong> Gr<strong>and</strong> Targhee access<br />

po<strong>in</strong>ts to backcountry ski<strong>in</strong>g <strong>in</strong> CTNF. For the purpose <strong>of</strong> this paper, we will focus on the<br />

visitor track<strong>in</strong>g data collected at the Death Canyon <strong>and</strong> Bradley-Taggart Lake trailheads<br />

<strong>in</strong> GTNP (see Figure 2).<br />

<strong>GPS</strong>-<strong>Based</strong> Data Collection <strong>and</strong> Data Analysis<br />

In all three case studies, <strong>GPS</strong> data on visitor routes were recorded us<strong>in</strong>g recreation-<br />

grade Garm<strong>in</strong> <strong>GPS</strong> 60 units (Table 1). <strong>GPS</strong> 60 models have 28 hours <strong>of</strong> battery life,<br />

storage <strong>of</strong> 1MB, <strong>and</strong> are Wide Area Augmentation System (WAAS) enabled allow<strong>in</strong>g<br />

for signal corrections <strong>and</strong> improved real-time accuracy. Each Garm<strong>in</strong> <strong>GPS</strong> 60 model<br />

costs approximately $190, can store track logs up to 10,000 po<strong>in</strong>ts, <strong>and</strong> is cited by the<br />

manufacture as hav<strong>in</strong>g a positional accuracy <strong>of</strong> with<strong>in</strong> 15 meters 95% <strong>of</strong> the time (Garm<strong>in</strong><br />

Ltd., 2010). <strong>Visitors</strong> were r<strong>and</strong>omly <strong>in</strong>tercepted at each trailhead accord<strong>in</strong>g to a sampl<strong>in</strong>g


Table 1. <strong>GPS</strong> sampl<strong>in</strong>g characteristics by study site.<br />

Study Data Number Response Number <strong>GPS</strong><br />

Site Collection <strong>of</strong> <strong>GPS</strong> Rate <strong>of</strong> Visitor Positional<br />

Dates Units Tracks Error<br />

Used Collected Estimate (m)<br />

Yosemite July 2009 30 82% 199 N/A<br />

(10 days)<br />

Rocky Mounta<strong>in</strong> July - August 2008 20 80% 301 6.40<br />

(13 days)<br />

Gr<strong>and</strong> Teton January - April 2009 10 90% 108 3.67<br />

(27 days)<br />

protocol <strong>of</strong> r<strong>and</strong>om days stratified by time <strong>of</strong> day <strong>and</strong> weekend <strong>and</strong> weekdays. All visitors<br />

were asked to voluntarily participate <strong>and</strong> only day use visitors were sampled. One <strong>GPS</strong> unit<br />

was given to a volunteer <strong>in</strong> each group <strong>and</strong> the visitor was asked to carry the unit clipped<br />

on to the outside <strong>of</strong> their pack for the duration <strong>of</strong> their hike or ski. The <strong>GPS</strong> unit recorded<br />

location po<strong>in</strong>ts at 15-second <strong>in</strong>tervals <strong>in</strong> YNP <strong>and</strong> RMNP or 5-second <strong>in</strong>tervals <strong>in</strong> GTNP.<br />

A shorter time <strong>in</strong>terval was used <strong>in</strong> GTNP to account for skiers’ greater speed <strong>of</strong> travel<br />

as compared to the hikers tracked <strong>in</strong> YNP <strong>and</strong> RMNP. The units were returned at the end<br />

<strong>of</strong> the visitor’s trip to technicians positioned at all possible exit trailheads. In the case <strong>of</strong><br />

trailheads <strong>in</strong> the GTNP, the <strong>GPS</strong> units could also be returned to a labeled drop box found<br />

at all possible exit trailheads.<br />

No units were broken, lost, or stolen <strong>in</strong> YNP or RMNP for a return rate <strong>of</strong> 100%. In<br />

GTNP two <strong>of</strong> the 10 units were lost out <strong>of</strong> a total <strong>of</strong> 108 samples. Each study site varied<br />

<strong>in</strong> topography <strong>and</strong> vegetation cover, which can affect signal reception. However, overall<br />

the unique environmental conditions at each study site did not <strong>in</strong>terfere significantly with<br />

data collection. In YNP, <strong>GPS</strong> track<strong>in</strong>g occurred mostly <strong>in</strong> high-elevation meadows with<br />

little canopy cover. The conditions <strong>in</strong> YNP resulted <strong>in</strong> very few miss<strong>in</strong>g or corrupt tracks;<br />

199 usable tracks out <strong>of</strong> 212 total tracks collected. In RMNP, the Bear Lake Road Corridor<br />

is located <strong>in</strong> a subalp<strong>in</strong>e ecosystem with dense to sparse tree cover <strong>and</strong> large cirque walls<br />

at some <strong>of</strong> the subalp<strong>in</strong>e lakes. Due to the areas <strong>of</strong> dense tree cover <strong>and</strong> mounta<strong>in</strong>ous<br />

environment, 301 usable tracks were collected out <strong>of</strong> 350 total tracks <strong>in</strong> RMNP. In GTNP,<br />

the backcountry ski routes range <strong>in</strong> elevation from approximately 2,000 meters to 3,500<br />

meters. The majority <strong>of</strong> backcountry ski<strong>in</strong>g occurs on the east slope <strong>of</strong> the Teton Range,<br />

which is characterized by steep, open slopes <strong>and</strong> deep canyons. At low elevations, there<br />

is significant conifer cover <strong>in</strong> many areas, but the cover did not affect <strong>GPS</strong> unit satellite<br />

reception. Occasionally, <strong>GPS</strong> units missed locations while visitors were travell<strong>in</strong>g <strong>in</strong> very<br />

deep, narrow canyons. In GTNP, most problems that occurred with <strong>GPS</strong> reception was<br />

usually due to visitors mov<strong>in</strong>g <strong>GPS</strong> units to <strong>in</strong>side their backpacks dur<strong>in</strong>g their trip or<br />

problems with low batteries due to colder conditions.<br />

To account for any possible site-specific, positional error associated with recreation<br />

grade <strong>GPS</strong> measures, calibration techniques were employed <strong>in</strong> RMNP <strong>and</strong> the Teton Range.<br />

Calibration also allowed for a verification <strong>of</strong> the accuracies calculated <strong>and</strong> displayed by the<br />

Garm<strong>in</strong> <strong>GPS</strong> 60, as no <strong>in</strong>formation on this process is available from the manufacturer due<br />

to the proprietary nature <strong>of</strong> the s<strong>of</strong>tware. In RMNP, a sub-meter Trimble GeoXT <strong>GPS</strong> unit<br />

47


48<br />

was used to map a calibration track along the center <strong>of</strong> the designated trail at each sampled<br />

trailhead. Before each sampl<strong>in</strong>g day began, a r<strong>and</strong>omly selected Garm<strong>in</strong> <strong>GPS</strong> 60 unit was<br />

used to record the same calibration track. Upon completion <strong>of</strong> data collection, all <strong>of</strong> the<br />

calibration tracks from Garm<strong>in</strong> <strong>GPS</strong> 60 units were compared to the high accuracy tracks<br />

assessed by the Trimble <strong>in</strong> ArcGIS s<strong>of</strong>tware. A Euclidian distance measure (a straight l<strong>in</strong>e<br />

distance measure between two po<strong>in</strong>ts) was used to determ<strong>in</strong>e the average positional error<br />

for each Garm<strong>in</strong> 60 <strong>GPS</strong> track. These error measures were then averaged to determ<strong>in</strong>e the<br />

overall positional error estimate for the Garm<strong>in</strong> <strong>GPS</strong> 60 dur<strong>in</strong>g the sampl<strong>in</strong>g period (Table<br />

1).<br />

In the Teton Range, due to logistical differences from RMNP, a slightly different<br />

calibration technique was used. At each trailhead sampled, a high accuracy po<strong>in</strong>t was<br />

recorded us<strong>in</strong>g a Trimble GeoXT <strong>GPS</strong> unit. At the start <strong>of</strong> each sampl<strong>in</strong>g day, a Garm<strong>in</strong><br />

60 <strong>GPS</strong> unit was r<strong>and</strong>omly selected <strong>and</strong> 75 po<strong>in</strong>ts were recorded at the same location at<br />

which the calibration po<strong>in</strong>t was recorded. A Euclidean distance was then calculated from<br />

each po<strong>in</strong>t recorded by the Garm<strong>in</strong> 60 <strong>GPS</strong> units to the calibration po<strong>in</strong>t; these values were<br />

averaged to determ<strong>in</strong>e the overall positional error (Table 1). No calibration methodologies<br />

were performed <strong>in</strong> YNP due to our previous experience with the method <strong>and</strong> because the<br />

project goal was to exam<strong>in</strong>e visitor travel routes rather than small spatial scale visitor use<br />

issues.<br />

The dataset result<strong>in</strong>g from <strong>GPS</strong>-based track<strong>in</strong>g methodologies is a series <strong>of</strong> po<strong>in</strong>t<br />

data that can then be exam<strong>in</strong>ed <strong>in</strong> a geographic <strong>in</strong>formation system (GIS). When exam<strong>in</strong>ed<br />

spatially, these data <strong>in</strong>herently comb<strong>in</strong>e visitor use levels <strong>and</strong> certa<strong>in</strong> behavioral aspects,<br />

such as visitors paus<strong>in</strong>g or congregat<strong>in</strong>g <strong>in</strong> one location. The data also <strong>in</strong>cludes additional<br />

attributes such as time, speed, <strong>and</strong> elevation. Analysis <strong>of</strong> the po<strong>in</strong>t data yields <strong>in</strong>formation<br />

on visitor densities <strong>and</strong> temporal <strong>and</strong> spatial patterns. When comb<strong>in</strong>ed with visitor surveys<br />

<strong>and</strong> total use estimation techniques, these data provide an important <strong>and</strong> highly accurate<br />

picture <strong>of</strong> visitor use <strong>and</strong> behavior.<br />

Visitor Use Estimation Data Collection <strong>and</strong> Data Analysis<br />

<strong>GPS</strong>-based measures can be used to supplement traditional visitor use estimation<br />

techniques. As such, total visitor use was estimated at selected attraction sites <strong>and</strong> trailheads<br />

<strong>in</strong> YNP <strong>and</strong> RMNP us<strong>in</strong>g active <strong>in</strong>frared automated monitors. These devices are commonly<br />

used by researchers <strong>and</strong> park managers to monitor recreation use levels <strong>in</strong> protected natural<br />

areas because they are relatively easy to <strong>in</strong>stall <strong>and</strong> operate. (Bates, Wallace, & Vaske,<br />

2007; Gracia-Longares, 2005; Pettebone, Newman, Beaton, Stack, & Gibson, 2008; Vaske<br />

& Donnelly, 2007).<br />

Similar approaches were used <strong>in</strong> both parks. For example, <strong>in</strong> RMNP, TrailMaster1550<br />

active <strong>in</strong>frared monitors were deployed at seven locations <strong>in</strong> the Bear Lake area to estimate<br />

visitor use at attraction sites <strong>and</strong> trailheads. At each study site, 10 hours <strong>of</strong> direct observation<br />

data were collected to calibrate results specific to each device. <strong>Based</strong> on the calibrations<br />

for each device, seasonal, daily, <strong>and</strong> hourly visitor use was estimated for each study site.<br />

Estimates <strong>of</strong> visitor use were comb<strong>in</strong>ed with data collected via <strong>GPS</strong> to determ<strong>in</strong>e spatially<br />

detailed total seasonal use along the Bear Lake trail system (Pettebone, 2009).<br />

Results <strong>and</strong> Discussion<br />

Spatial Aspects <strong>of</strong> Visitor Use<br />

The <strong>GPS</strong> techniques employed <strong>in</strong> the three studies allow for the exam<strong>in</strong>ation <strong>of</strong> spatial<br />

patterns <strong>of</strong> visitor use at a much more detailed level than is possible through observational<br />

or survey techniques. At the relatively large spatial scale <strong>of</strong> a park or management unit,


<strong>GPS</strong>-based track<strong>in</strong>g data can be mapped to show the extent <strong>of</strong> use with<strong>in</strong> the system<br />

(Figures 1 <strong>and</strong> 2). For example, <strong>in</strong> YNP, visitors were tracked with<strong>in</strong> the Tuolumne<br />

Meadows trail system <strong>and</strong> mapp<strong>in</strong>g <strong>of</strong> these data <strong>in</strong>dicate the spatial extent <strong>of</strong> day use<br />

hikers orig<strong>in</strong>at<strong>in</strong>g from the Tuolumne visitor center trailheads (Figure 1). This <strong>in</strong>formation<br />

is relevant to managers <strong>in</strong> provid<strong>in</strong>g a thorough underst<strong>and</strong><strong>in</strong>g <strong>of</strong> the nature <strong>of</strong> hik<strong>in</strong>g<br />

use <strong>in</strong> this trail system. The detail provided by <strong>GPS</strong>-based techniques, even at a large<br />

spatial scale, is greater than that which could be provided by traditional techniques, which<br />

typically provide only total use on trail segments where they are located.<br />

Information on the overall spatial extent <strong>of</strong> visitation is also particularly valuable<br />

<strong>in</strong> situations where the visitor use patterns are not as predictable—where most <strong>of</strong> the<br />

visitation is occurr<strong>in</strong>g <strong>of</strong>f <strong>of</strong> a designated trail system. This is illustrated <strong>in</strong> the analysis <strong>of</strong><br />

data collected <strong>in</strong> the GTNP study <strong>of</strong> backcountry skiers (Figure 2). Data <strong>of</strong> this k<strong>in</strong>d are<br />

useful <strong>in</strong> identify<strong>in</strong>g locations, densities, <strong>and</strong> temporal patterns <strong>of</strong> <strong>of</strong>f-trail use <strong>and</strong>, <strong>in</strong> this<br />

case, are able to be directly compared with <strong>GPS</strong>-collared wildlife locations <strong>and</strong> habitat use<br />

patterns. <strong>GPS</strong> track<strong>in</strong>g data can be easily <strong>in</strong>corporated <strong>in</strong>to statistical models as a predictor<br />

variable <strong>of</strong> wildlife distribution.<br />

The spatial components <strong>of</strong> the backcountry skier tracks (distance <strong>of</strong> backcountry travel<br />

routes, <strong>of</strong> vary<strong>in</strong>g densities, to <strong>GPS</strong>-collared bighorn sheep locations) can be <strong>in</strong>cluded,<br />

along with several additional predictor variables, <strong>in</strong>to a resource selection function (RSF)<br />

model<strong>in</strong>g procedure for w<strong>in</strong>ter habitat use (Sawyer et al., 2006). In GTNP, visitor use<br />

data was collected concurrently with <strong>GPS</strong>-collared bighorn sheep data. In future work,<br />

the detailed location data from both bighorn sheep <strong>and</strong> backcountry visitors will allow<br />

for the determ<strong>in</strong>ation <strong>of</strong> how various spatial <strong>and</strong> temporal patterns <strong>of</strong> backcountry ski<strong>in</strong>g<br />

affect bighorn sheep w<strong>in</strong>ter habitat use. W<strong>in</strong>ter backcountry recreation will be <strong>in</strong>cluded as<br />

a predictor variable <strong>in</strong> the RSF (as distance to backcountry use areas <strong>of</strong> vary<strong>in</strong>g densities<br />

<strong>of</strong> use) to determ<strong>in</strong>e if bighorn sheep avoid backcountry recreation routes, even if these<br />

areas have been identified by the RSF as suitable w<strong>in</strong>ter habitat. Specifically, the RSF<br />

can determ<strong>in</strong>e if a threshold <strong>of</strong> visitor use at which bighorn sheep ab<strong>and</strong>on suitable w<strong>in</strong>ter<br />

habitat areas exists. These model<strong>in</strong>g procedures are especially useful to wildlife managers<br />

to identify areas <strong>of</strong> potential <strong>in</strong>teraction between recreationists <strong>and</strong> wildlife.<br />

The detail associated with <strong>GPS</strong> track<strong>in</strong>g data, where positional errors can be estimated,<br />

also allows for analysis at smaller spatial scales such as dest<strong>in</strong>ation po<strong>in</strong>ts. In these cases,<br />

exam<strong>in</strong>ation <strong>of</strong> particular aspects <strong>of</strong> visitor behavior, <strong>in</strong>clud<strong>in</strong>g wait<strong>in</strong>g times at the<br />

dest<strong>in</strong>ation po<strong>in</strong>t <strong>and</strong> exam<strong>in</strong>ation <strong>of</strong> <strong>of</strong>f-trail use may be particularly relevant to manag<strong>in</strong>g<br />

for visitor experience <strong>and</strong> resource protection. In the case <strong>of</strong> RMNP, the error calculated<br />

from the calibration procedures was used to create a 12.8m buffer around designated trails.<br />

All visitor po<strong>in</strong>ts with<strong>in</strong> the buffer were considered to be “on trail.” Specific po<strong>in</strong>ts <strong>of</strong><br />

<strong>in</strong>terest can then be exam<strong>in</strong>ed more closely to explore the details <strong>of</strong> visitor use <strong>in</strong> these<br />

dispersed-use sett<strong>in</strong>gs. For example, <strong>in</strong> RMNP, <strong>of</strong>f-trail use was exam<strong>in</strong>ed at Alberta Falls<br />

(Figure 3). Off-trail use can be given further context when comb<strong>in</strong>ed with <strong>GPS</strong>-recorded<br />

visitor impacts such as visitor created trails <strong>and</strong> sites. The comb<strong>in</strong>ation <strong>of</strong> visitor-impact<br />

data <strong>and</strong> <strong>GPS</strong> track<strong>in</strong>g data can highlight how visitors are access<strong>in</strong>g <strong>of</strong>f trail areas <strong>and</strong> how<br />

visitors are us<strong>in</strong>g areas that have already experienced resource change.<br />

Underst<strong>and</strong><strong>in</strong>g the typical spatial patterns <strong>of</strong> visitor use can <strong>in</strong>form decisions related<br />

to designated trail management. Also, by underst<strong>and</strong><strong>in</strong>g spatial patterns <strong>of</strong> <strong>of</strong>f-trail use,<br />

managers can evaluate the effectiveness <strong>of</strong> current management techniques to discourage<br />

<strong>of</strong>f-trail use. The level <strong>of</strong> accuracy <strong>and</strong> detail provided by <strong>GPS</strong>-based measures, at both<br />

the large <strong>and</strong> small spatial scale, allows managers to identify <strong>and</strong> focus on areas <strong>of</strong> most<br />

concern for resource change <strong>and</strong> dim<strong>in</strong>ished visitor experience. Traditional techniques,<br />

such as observational studies <strong>and</strong> survey methodologies may not provide the same level <strong>of</strong><br />

detail or accuracy, especially <strong>in</strong> situations <strong>of</strong> dispersed visitor use.<br />

49


50<br />

Figure 1. Extent <strong>of</strong> hik<strong>in</strong>g use orig<strong>in</strong>at<strong>in</strong>g from trailheads <strong>in</strong> Tuolumne Meadows trail<br />

system <strong>in</strong> YNP. Stars mark trailheads where sampl<strong>in</strong>g occurred.


Figure 2. Extent <strong>of</strong> backcountry ski use from trailheads <strong>in</strong> GTNP. Stars make trailheads<br />

where sampl<strong>in</strong>g occurred.<br />

51


52<br />

Figure 3. <strong>GPS</strong> track<strong>in</strong>g <strong>of</strong> <strong>of</strong>f-trail travel by visitors at Alberta Falls <strong>in</strong> RMNP.<br />

Density Analysis<br />

Visitor po<strong>in</strong>t data can be used to calculate a density <strong>of</strong> visitor track<strong>in</strong>g po<strong>in</strong>ts. High<br />

visitor densities can be caused by overall high levels <strong>of</strong> use or by a few visitors stay<strong>in</strong>g <strong>in</strong><br />

an area for an extended period <strong>of</strong> time. Visitor use density can be exam<strong>in</strong>ed at a systemwide<br />

level to highlight areas <strong>of</strong> high use that can then be analyzed at a more detailed<br />

level (Figure 4). Once sites for further <strong>in</strong>vestigation are identified, a density analysis can<br />

be completed for popular hik<strong>in</strong>g dest<strong>in</strong>ations such as Dog Lake <strong>in</strong> YNP (Figure 5). A<br />

density analysis <strong>of</strong> the visitors tracked to Dog Lake show that the highest densities <strong>of</strong><br />

po<strong>in</strong>ts are found where the designated trail first connects to the lake <strong>and</strong> at various spots<br />

along the edge <strong>of</strong> Dog Lake. The density analysis also shows that there is concentrated<br />

use at an area <strong>of</strong>f <strong>of</strong> the designated trail on the northwest shore <strong>of</strong> Dog Lake. Managers<br />

can use density analyses to highlight areas that may be at risk for changes to resource<br />

conditions or dim<strong>in</strong>ished visitor experience from crowd<strong>in</strong>g or conflict. Further analysis<br />

can be performed us<strong>in</strong>g the same <strong>GPS</strong>-based track<strong>in</strong>g data to exam<strong>in</strong>e temporal <strong>and</strong> spatial<br />

patterns at these areas to better underst<strong>and</strong> visitor behavior at these popular dest<strong>in</strong>ations.<br />

Temporal Aspects <strong>of</strong> Visitor Use<br />

<strong>GPS</strong> units record visitor location at a selected time <strong>in</strong>terval. As such, the track<strong>in</strong>g<br />

data can be analyzed to better underst<strong>and</strong> the temporal patterns <strong>of</strong> visitor use <strong>in</strong> an area. At<br />

the large scale, characteristics for an entire visit can be determ<strong>in</strong>ed. For example, visitortrack<strong>in</strong>g<br />

data were used to determ<strong>in</strong>e the average time visitors spent <strong>in</strong> each study area<br />

(Table 2). <strong>Visitors</strong> spent the most time <strong>in</strong> the GTNP system, averag<strong>in</strong>g 6 hours <strong>and</strong> 28<br />

m<strong>in</strong>utes. In YNP, the visitors tracked spent an average <strong>of</strong> 5 hours <strong>and</strong> 20 m<strong>in</strong>utes <strong>in</strong> the<br />

Tuolumne Meadows trail system. While <strong>in</strong> RMNP, visitors spent an average <strong>of</strong> 2 hours <strong>and</strong><br />

30 m<strong>in</strong>utes <strong>in</strong> the Bear Lake Road Corridor trail system. An exam<strong>in</strong>ation <strong>of</strong> the temporal


Figure 4. Density analysis <strong>of</strong> visitor use po<strong>in</strong>ts <strong>in</strong> the Tuolumne Meadows trail system<br />

<strong>in</strong> YNP.<br />

Table 2. Analysis <strong>of</strong> temporal patterns <strong>of</strong> visitor use.<br />

Location Average Total Time Max Time M<strong>in</strong> Time St<strong>and</strong>ard<br />

<strong>in</strong> Area <strong>in</strong> Area <strong>in</strong> Area Deviation<br />

(h:mm) (h:mm) (h:mm)<br />

Tuolumne Meadows<br />

(Yosemite) 5:20 11:08 0:29 2.33<br />

Bear Lake<br />

(Rocky Mounta<strong>in</strong>) 2:30 8:00 0:04 0.07<br />

Gr<strong>and</strong> Teton 6:28 13:52 0:32 2.51<br />

53


54<br />

Figure 5. Density analysis <strong>of</strong> visitor use po<strong>in</strong>ts at Dog Lake <strong>in</strong> Tuolumne Meadows, YNP.<br />

component <strong>of</strong> visitor use at a large scale can <strong>in</strong>form managers about length <strong>of</strong> stay <strong>in</strong> an<br />

area or on a trail system.<br />

Large-scale temporal data can also be <strong>in</strong>tegrated with other studies. For example,<br />

the temporal aspects <strong>of</strong> visitor hikes collected <strong>in</strong> RMNP were used <strong>in</strong> comb<strong>in</strong>ation<br />

with a transportation noise model <strong>of</strong> the park to underst<strong>and</strong> visitors’ experiences <strong>of</strong> the<br />

park’s soundscape. Specifically, the <strong>GPS</strong> visitor data <strong>and</strong> maps <strong>of</strong> transportation-related<br />

noise levels were analyzed spatially. GIS spatial statistics were applied to these data to<br />

estimate the amount <strong>of</strong> time <strong>and</strong> distance visitors must hike from trailheads away from the<br />

transportation corridor to experience natural sounds. Estimates were also generated for the<br />

proportion <strong>of</strong> visitors who experience at least 15 m<strong>in</strong>utes <strong>of</strong> natural sounds <strong>and</strong> quiet. At<br />

the time <strong>of</strong> the study, the National Park Service had not def<strong>in</strong>ed a threshold for road noise,<br />

beyond which natural sounds <strong>and</strong> quiet are compromised. Thus, a range <strong>of</strong> example road<br />

noise thresholds were evaluated to estimate the proportion <strong>of</strong> visitors who experience at<br />

least 15 m<strong>in</strong>utes <strong>of</strong> natural sounds <strong>and</strong> quiet. The example road noise thresholds used <strong>in</strong> the<br />

analysis <strong>in</strong>clude ≤25 dBA (nighttime ambient natural sound level measured <strong>in</strong> the study),<br />

≤30 dBA <strong>and</strong> ≤35 dBA (daytime ambient natural sound levels), <strong>and</strong> ≤65 dBA (the level at<br />

which noise <strong>in</strong>terferes with conversational tones).<br />

Temporal patterns <strong>of</strong> use can also be exam<strong>in</strong>ed at a small scale such as at specific<br />

sites <strong>of</strong> <strong>in</strong>terest. In RMNP, visitors frequently travel <strong>of</strong>f-trail <strong>in</strong> an area <strong>of</strong> dispersed<br />

use adjacent to Alberta Falls (Figure 2). By us<strong>in</strong>g the positional error calculated from<br />

calibration techniques to elim<strong>in</strong>ate all on trail use from the analysis <strong>and</strong> us<strong>in</strong>g the temporal


data collected from the <strong>GPS</strong> units, it was determ<strong>in</strong>ed that 46% <strong>of</strong> visitors that were tracked<br />

travel<strong>in</strong>g along the Glacier Gorge trail left the designated trail adjacent to Alberta Falls <strong>and</strong><br />

spent, on average, 17 m<strong>in</strong>utes <strong>of</strong>f trail. Visitor use can also be analyzed by the distance<br />

traveled from the designated trail, for example at Alberta Falls, the area <strong>of</strong> dispersed<br />

use was split <strong>in</strong>to two <strong>of</strong>f-trail zones; one near the designated trail <strong>and</strong> one far from the<br />

designated trail. The data result<strong>in</strong>g from this analysis can then be <strong>in</strong>corporated <strong>in</strong> model<strong>in</strong>g<br />

efforts to exam<strong>in</strong>e dispersed use with<strong>in</strong> <strong>of</strong>f trail areas.<br />

Integration with Visitor Use Estimation <strong>and</strong> Survey Techniques<br />

Estimates <strong>of</strong> use level are important for managers <strong>in</strong> terms <strong>of</strong> <strong>in</strong>form<strong>in</strong>g issues such<br />

as the potential for resource change <strong>and</strong> experiential impacts such as crowd<strong>in</strong>g. Automatic<br />

counter data can be comb<strong>in</strong>ed with <strong>GPS</strong>-based measurements to ga<strong>in</strong> a better underst<strong>and</strong><strong>in</strong>g<br />

<strong>of</strong> visitor use for popular dest<strong>in</strong>ations. For example, <strong>in</strong> RMNP, automatic visitor counters<br />

were placed on the trailheads that were sampled us<strong>in</strong>g <strong>GPS</strong>-based methodologies. An<br />

automatic visitor counter was placed at the Bear Lake trailhead, which provides access<br />

to the Emerald Lake trail <strong>and</strong> three alp<strong>in</strong>e lakes. From the <strong>GPS</strong>-based measures recorded<br />

<strong>and</strong> the visitor counters, it can be determ<strong>in</strong>ed that 28% <strong>of</strong> visitors traveled to a dest<strong>in</strong>ation<br />

along the Emerald Lake trail. The average seasonal use for the Bear Lake trailhead, as<br />

determ<strong>in</strong>ed by the automated visitor counters can then be comb<strong>in</strong>ed with the <strong>GPS</strong>-based<br />

results <strong>of</strong> travel to dest<strong>in</strong>ations along the Emerald Lake trail to estimate overall seasonal<br />

use patterns along the designated trail.<br />

Strategic placement <strong>of</strong> automatic visitor counters can also be comb<strong>in</strong>ed with <strong>GPS</strong>based<br />

measures to determ<strong>in</strong>e use levels at specific areas <strong>of</strong> visitor <strong>in</strong>terest or <strong>of</strong>f-trail<br />

dest<strong>in</strong>ations. <strong>GPS</strong>-based measurements provide an additional layer <strong>of</strong> detail to traditional<br />

visitor use-estimation techniques, which can only provide an estimate <strong>of</strong> use level at the<br />

specific location <strong>of</strong> the counter mechanism. <strong>GPS</strong>-track<strong>in</strong>g methodologies can provide<br />

<strong>in</strong>formation regard<strong>in</strong>g exactly where visitors are go<strong>in</strong>g <strong>and</strong> the routes that visitors are us<strong>in</strong>g<br />

to get to their dest<strong>in</strong>ations.<br />

<strong>GPS</strong>-based track<strong>in</strong>g data can effectively provide spatial <strong>and</strong> temporal data <strong>and</strong> be used<br />

to complement automated visitor counters <strong>in</strong> use estimation, but the result<strong>in</strong>g dataset does<br />

not conta<strong>in</strong> any <strong>in</strong>formation about visitor characteristics. However, the visitor-track<strong>in</strong>g<br />

methodologies discussed here can be comb<strong>in</strong>ed with traditional survey techniques. In<br />

RMNP, visitors who participated <strong>in</strong> the <strong>GPS</strong>-based visitor track<strong>in</strong>g study were asked to<br />

complete a short survey follow<strong>in</strong>g their hike. The surveys were coded so that <strong>in</strong>dividual<br />

<strong>GPS</strong> tracks could be l<strong>in</strong>ked to the visitor’s survey (Table 3). For example, Euclidean<br />

distance calculations were computed for <strong>in</strong>dividual visitors <strong>and</strong> the average distance that<br />

each <strong>in</strong>dividual traveled <strong>of</strong>f <strong>of</strong> the designated trail can be calculated (Table 3). <strong>Visitors</strong> were<br />

asked whether or not they hiked <strong>of</strong>f-trail to avoid feel<strong>in</strong>g crowded with results show<strong>in</strong>g<br />

that some visitors who answered ‘no’ to this question were recorded as travel<strong>in</strong>g <strong>of</strong>f-trail.<br />

The comb<strong>in</strong>ation <strong>of</strong> survey <strong>and</strong> <strong>GPS</strong>-based techniques allows for a comparison between<br />

reported behavior by visitors <strong>and</strong> actual, measured behaviors.<br />

It is possible that some visitors hiked <strong>of</strong>f-trail for reasons other than feel<strong>in</strong>g crowded<br />

<strong>and</strong> thus answered ‘no’ to this question on the survey; however, the comb<strong>in</strong>ation <strong>of</strong> <strong>GPS</strong>based<br />

methodology with survey techniques provides a means <strong>of</strong> comb<strong>in</strong><strong>in</strong>g <strong>in</strong>dividual<br />

visitor behavior with visitor characteristics. Survey techniques allow for the stratification<br />

<strong>of</strong> <strong>GPS</strong>-based track<strong>in</strong>g data by visitor characteristics, such as knowledge <strong>of</strong> Leave No<br />

Trace practices or activity type, <strong>and</strong> for comparisons <strong>of</strong> visitor behavior across groups. The<br />

comb<strong>in</strong>ation <strong>of</strong> survey results with <strong>GPS</strong>-based methodology allows managers to exam<strong>in</strong>e<br />

visitor use patterns stratified by user group. This <strong>in</strong>formation could further underst<strong>and</strong><strong>in</strong>g<br />

<strong>of</strong> the needs <strong>and</strong> behaviors <strong>of</strong> different groups <strong>and</strong> how to target certa<strong>in</strong> user groups based<br />

on behavior.<br />

55


56<br />

Table 3. Survey results from r<strong>and</strong>omly selected visitors at the Glacier Gorge<br />

Trailhead at RMNP.<br />

Visitor ID Distance Visitor Traveled Off-Trail 1 Hike Off-Trail To<br />

Avoid Feel<strong>in</strong>g Crowded?<br />

M<strong>in</strong> (m) Max (m) Mean (m)<br />

126 0 2.73 0.14 No<br />

148 0 28.07 4.09 No<br />

275 0 8.18 0.69 No<br />

309 0 2.73 0.14 No<br />

55 0 50.12 4.96 Yes<br />

128 0 8.18 1.12 Yes<br />

146 0 17.46 2.08 Yes<br />

295 0 53.70 3.39 Yes<br />

1 Euclidian distance calculated to trail buffer<br />

Conclusion<br />

<strong>GPS</strong>-based track<strong>in</strong>g methodologies provide accurate <strong>and</strong> detailed datasets that <strong>of</strong>fer<br />

<strong>in</strong>formation that cannot be practically collected us<strong>in</strong>g traditional methods for estimat<strong>in</strong>g<br />

visitor use. <strong>GPS</strong> methodologies are an established means <strong>of</strong> gather<strong>in</strong>g spatial <strong>and</strong> behavioral<br />

<strong>in</strong>formation <strong>in</strong> the wildlife sciences (Bowmen, Kochanny, Demarais, & Leopold, 2000;<br />

Burger & Shaffer, 2008; Rutter, 2007) <strong>and</strong> provide very valuable <strong>in</strong>formation to wildlife<br />

managers. This research shows that <strong>GPS</strong> methods can be employed successfully to further<br />

underst<strong>and</strong> visitor use <strong>in</strong> park <strong>and</strong> protected area management.<br />

<strong>GPS</strong> approaches do present some challenges <strong>and</strong> limitations. Logistically, an effective<br />

methodology needs to be devised to adm<strong>in</strong>ister <strong>and</strong> retrieve the <strong>GPS</strong> units used (Schaick<br />

& van der Spek, 2008). In complicated trail systems, to ensure a high return rate <strong>of</strong> units,<br />

it is important to have technicians or drop boxes located at all possible exit locations. Also,<br />

each unit should be labeled with <strong>in</strong>structions regard<strong>in</strong>g how to return the unit <strong>in</strong> the event<br />

that the visitor cannot f<strong>in</strong>d a technician or drop box. The battery life <strong>and</strong> data storage <strong>of</strong> the<br />

units employed <strong>in</strong> this study is a limitation if <strong>GPS</strong>-based methodology is to be utilized <strong>in</strong><br />

a backcountry, multi-day trip sett<strong>in</strong>g, but technology is be<strong>in</strong>g developed that will work <strong>in</strong><br />

this situation as well (Rupf, Koechli, Haider, Skov-Petersen, & Probstl, 2010).<br />

The issue <strong>of</strong> positional error <strong>and</strong> satellite reception can become a problem <strong>in</strong> certa<strong>in</strong><br />

environmental sett<strong>in</strong>gs, <strong>and</strong> therefore calibration techniques can be helpful to quantify the<br />

site-specific error associated with the track<strong>in</strong>g data. Recent <strong>GPS</strong> technological advances<br />

have resulted <strong>in</strong> more sensitive, accurate h<strong>and</strong>held units such as the Garm<strong>in</strong> <strong>GPS</strong> 60Cx <strong>and</strong><br />

<strong>GPS</strong> 60 CSx. However, the use <strong>of</strong> these updated units <strong>in</strong> <strong>GPS</strong>-based studies may be less<br />

feasible as they are more expensive than less sophisticated units <strong>and</strong> have a shorter battery<br />

life (Garm<strong>in</strong> Ltd., 2010). Regardless, as <strong>GPS</strong> technology cont<strong>in</strong>ues to improve, calibration<br />

<strong>and</strong> accuracy issues may become less <strong>of</strong> a concern.<br />

Data process<strong>in</strong>g <strong>and</strong> analysis are also significant considerations, as the approaches<br />

illustrated require some knowledge <strong>of</strong> GIS to edit <strong>and</strong> analyze the data collected. Recently<br />

developed extensions for ArcMap (a GIS s<strong>of</strong>tware program) allow for quick <strong>and</strong> easy<br />

importation <strong>of</strong> large numbers <strong>of</strong> <strong>GPS</strong> tracks <strong>in</strong>to a GIS environment. Once <strong>in</strong> a GIS<br />

environment, a basic knowledge <strong>of</strong> ArcGIS is required for the data-clean<strong>in</strong>g process as<br />

corrupt files are easily identified <strong>and</strong> many <strong>of</strong> the analysis presented here (po<strong>in</strong>t density,


straight l<strong>in</strong>e distance calculations, time analyses) can be completed us<strong>in</strong>g available tools<br />

<strong>in</strong> ArcMap (Schaick & van der Spek, 2008). An overrid<strong>in</strong>g concern is that the approach<br />

illustrated here, particularly the density analysis, is a result <strong>of</strong> both visitor use levels<br />

<strong>and</strong> visitor behavior—high-po<strong>in</strong>t densities can be the result <strong>of</strong> either high total use or<br />

visitors paus<strong>in</strong>g <strong>and</strong> congregat<strong>in</strong>g while the <strong>GPS</strong> is collect<strong>in</strong>g data. These po<strong>in</strong>t densities<br />

were applicable for the larger social <strong>and</strong> ecological projects for which these methods<br />

were developed, but other <strong>in</strong>vestigators may be <strong>in</strong>terested <strong>in</strong> assess<strong>in</strong>g use <strong>and</strong> behavior<br />

<strong>in</strong>dependently. In this case, some additional methodological development is needed.<br />

Despite these limitations, <strong>GPS</strong>-based methodologies have clear advantages <strong>and</strong><br />

applications. The time dem<strong>and</strong> on visitors is m<strong>in</strong>imal <strong>and</strong> less tra<strong>in</strong><strong>in</strong>g is required for<br />

staff to conduct a <strong>GPS</strong>-based track<strong>in</strong>g study compared to other techniques. In the case<br />

studies presented, there were low refusal rates for participation that resulted <strong>in</strong> very ample<br />

datasets be<strong>in</strong>g collected <strong>in</strong> a relatively short period <strong>of</strong> time. <strong>GPS</strong> technology allows for<br />

the exam<strong>in</strong>ation <strong>of</strong> subtle visitor movements such as <strong>of</strong>f-trail use that would be difficult<br />

or even impossible to measure accurately with traditional techniques. <strong>GPS</strong>-based track<strong>in</strong>g<br />

datasets conta<strong>in</strong> valuable descriptive data such as time, speed, direction, <strong>and</strong> elevation <strong>and</strong><br />

the method produces potentially less biased datasets compared to observational studies,<br />

diaries, <strong>and</strong> survey techniques. The case studies presented demonstrate just a few examples<br />

<strong>of</strong> analysis that can be conducted us<strong>in</strong>g <strong>GPS</strong>-based tracks. Other possible data analyses<br />

techniques <strong>in</strong>clude time series analysis, three-dimensional displays <strong>of</strong> density, analysis <strong>of</strong><br />

visitor speed, <strong>and</strong> stratification <strong>of</strong> results by activity type characteristics (Schaick & van<br />

der Spek, 2008).<br />

As demonstrated through the case studies exam<strong>in</strong>ed <strong>in</strong> this paper, the methods<br />

presented can be implemented <strong>in</strong> a range <strong>of</strong> sett<strong>in</strong>gs to address a variety <strong>of</strong> managerial issues<br />

or problems. There is potential for the <strong>in</strong>formation provided by <strong>GPS</strong>-based techniques to<br />

lead to more <strong>in</strong>formed management decisions due to the high levels <strong>of</strong> accuracy <strong>and</strong> detail<br />

that cannot be practically collected us<strong>in</strong>g traditional methodologies. Future implementation<br />

<strong>and</strong> development <strong>of</strong> the techniques presented here can serve to exp<strong>and</strong> the utility <strong>and</strong><br />

worth<strong>in</strong>ess <strong>of</strong> the <strong>GPS</strong>-based measures as an emerg<strong>in</strong>g technique to underst<strong>and</strong> visitor use<br />

<strong>in</strong> parks <strong>and</strong> protected areas.<br />

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