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Linking Culture and the Environment

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Y.-F. Leung et al. 25<br />

Amount of impact<br />

+<br />

Infection points<br />

(a)<br />

(b)<br />

0<br />

Amount of use<br />

+<br />

Fig. 2.2. Generalized relationships between visitor use <strong>and</strong> resultant resource impacts.<br />

Visitor behaviour can also influence <strong>the</strong> type <strong>and</strong> extent of environmental<br />

impacts. Vegetation <strong>and</strong> soil disturbance may be avoided or minimized<br />

by selecting resistant surfaces or vegetation for travel <strong>and</strong> camping.<br />

Area of disturbance is minimized when visitors constrain <strong>the</strong>ir activities<br />

to existing disturbed surfaces – by staying on established trails, travelling<br />

single file in <strong>the</strong> centre of <strong>the</strong> tread, or camping within core areas of established<br />

sites. Such low-impact travel <strong>and</strong> camping skills are <strong>the</strong> focus of <strong>the</strong><br />

Leave No Trace outdoor skills <strong>and</strong> ethics programme, which will be<br />

described shortly.<br />

Effectiveness of management interventions<br />

Protected area managers can avoid or minimize visitor impacts by influencing<br />

factors related to both visitation <strong>and</strong> <strong>the</strong> environment within which<br />

use occurs. Visitation can be shifted from fragile (e.g. critical wildlife habitats)<br />

to more resistant or resilient locations. Visitor activities can be concentrated<br />

on hardened sites or facilities maintained to sustain high levels of<br />

use. Higher impact activities can be prohibited or restricted to areas best<br />

able to accommodate such use. Low-impact visitor behaviour can be<br />

encouraged through education or required through regulations. Finally,<br />

rehabilitation efforts can facilitate recovery on recreation sites unacceptably<br />

degraded by visitor use.<br />

Recent years have seen increasing attention paid to empirically examining<br />

<strong>the</strong> effectiveness of such management <strong>and</strong> restoration actions as mentioned<br />

above. For example, Reid <strong>and</strong> Marion (2005) monitored campsite impacts in<br />

Shen<strong>and</strong>oah National Park in Virginia, USA, before <strong>and</strong> after a change of<br />

camping policy in 2000. They found that newly implemented visitor containment<br />

measures using designated <strong>and</strong> established sites resulted in a 51%<br />

reduction of l<strong>and</strong> disturbance <strong>and</strong> a 44% reduction of vegetation loss. Several<br />

o<strong>the</strong>r studies also supported <strong>the</strong> effectiveness of designated site policy in<br />

controlling resource impacts by visitors (Marion <strong>and</strong> Farrell, 2002) or packstock<br />

(Spildie et al., 2000). Similarly, Marion (1995) found a 50% reduction in

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