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Recreation and large mammal activity in an urban nature reserve

Recreation and large mammal activity in an urban nature reserve

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BIOLOGICAL CONSERVATION 133 (2006) 107– 117 115(Miller et al., 2001). Although we did not f<strong>in</strong>d a clear <strong><strong>an</strong>d</strong> consistentpattern of avoid<strong>an</strong>ce of hum<strong>an</strong> recreation by deer, theprobability of detect<strong>in</strong>g deer dur<strong>in</strong>g the day was lower with<strong>in</strong>creas<strong>in</strong>g levels of hum<strong>an</strong> recreation.If <strong>large</strong> <strong>mammal</strong>s are somewhat toler<strong>an</strong>t, albeit <strong>in</strong> differ<strong>in</strong>gdegrees, to hum<strong>an</strong> <strong>in</strong>trusion with<strong>in</strong> the NROC, this maypartially result from lack of hunt<strong>in</strong>g or trapp<strong>in</strong>g <strong>in</strong> the <strong>reserve</strong>,activities that c<strong>an</strong> result <strong>in</strong> the <strong>in</strong>creased war<strong>in</strong>essof both deer (Kufeld et al., 1988; Naugle et al., 1997; Kilpatrick<strong><strong>an</strong>d</strong> Lima, 1999) <strong><strong>an</strong>d</strong> carnivores (Andelt, 1985; McClennen<strong><strong>an</strong>d</strong> Shackleton, 1989; Fr<strong>an</strong>k <strong><strong>an</strong>d</strong> Woodroffe, 2001).Indeed, desensitization of <strong>large</strong> <strong>mammal</strong>s to hum<strong>an</strong> recreationmay result from habituation, def<strong>in</strong>ed as decreasedresponsiveness result<strong>in</strong>g from repeated applications of neutralstimuli (Whittaker <strong><strong>an</strong>d</strong> Knight, 1998). The ability tohabituate to predictable <strong><strong>an</strong>d</strong> recurrent hum<strong>an</strong> use of recreationaltrails may be <strong>an</strong> import<strong>an</strong>t behavioral adaptation forwildlife <strong>in</strong> urb<strong>an</strong> areas, allow<strong>in</strong>g them to cont<strong>in</strong>ue normalbehaviors, such as rest<strong>in</strong>g, forag<strong>in</strong>g or breed<strong>in</strong>g, when confrontedwith cont<strong>in</strong>ued hum<strong>an</strong> <strong>activity</strong> (Whittaker <strong><strong>an</strong>d</strong>Knight, 1998). However, habituated urb<strong>an</strong> wildlife might beless likely to avoid contact with hum<strong>an</strong>s, <strong><strong>an</strong>d</strong> thus may bemore likely to be attracted to <strong>an</strong>thropogenic food sourcessuch as lawns or gardens for ungulates (Lubow et al., 2002;Rub<strong>in</strong> et al., 2002) or pets, trash, <strong><strong>an</strong>d</strong> cultivated fruits for carnivores(MacCracken, 1982; McClure et al., 1995; Qu<strong>in</strong>n,1997b; Crooks <strong><strong>an</strong>d</strong> Soulé, 1999; Fedri<strong>an</strong>i et al., 2001). Habituationmay also <strong>in</strong>crease wildlife aggression towards hum<strong>an</strong>s,or render wildlife more vulnerable to hunters, poach<strong>in</strong>g, orroad-kill (Jones <strong><strong>an</strong>d</strong> Witham, 1990; Knight <strong><strong>an</strong>d</strong> Gutzwiller,1995; Whittaker <strong><strong>an</strong>d</strong> Knight, 1998; Kloppers et al., 2005). Becausehabituation c<strong>an</strong> <strong>in</strong>crease the probability of hum<strong>an</strong>wildlifeconflicts, it is considered <strong>an</strong> emerg<strong>in</strong>g problem <strong>in</strong>m<strong>an</strong>y urb<strong>an</strong> areas (Thompson <strong><strong>an</strong>d</strong> Henderson, 1998; Klopperset al., 2005).A priority for future research is experimental studies tofurther explore potential relationships between hum<strong>an</strong> recreation<strong><strong>an</strong>d</strong> wildlife <strong>in</strong> metropolit<strong>an</strong> <strong>reserve</strong> systems. For example,experimentally exam<strong>in</strong><strong>in</strong>g wildlife <strong>activity</strong> prior to <strong><strong>an</strong>d</strong>after the admitt<strong>an</strong>ce or cessation of specific recreationalactivities <strong>in</strong> <strong>an</strong> area, preferentially with control areas withno such treatment, would help identify causal mech<strong>an</strong>isms<strong><strong>an</strong>d</strong> hence allow stronger <strong>in</strong>ference regard<strong>in</strong>g species-specificresponses to recreational groups. Further, when <strong>in</strong>terpret<strong>in</strong>gwildlife responses to hum<strong>an</strong> <strong>in</strong>trusion, it is also import<strong>an</strong>tto consider the costs <strong><strong>an</strong>d</strong> benefits associated with avoid<strong>in</strong>ghum<strong>an</strong> disturb<strong>an</strong>ce. Benefits <strong>in</strong>clude avoid<strong>in</strong>g the disturb<strong>an</strong>ce,but costs might <strong>in</strong>clude energy expenditures <strong><strong>an</strong>d</strong> risksof predation while mov<strong>in</strong>g to do so. It is often assumed thatspecies behaviorally avoid<strong>in</strong>g disturb<strong>an</strong>ces are most susceptibleto them, but behavioral avoid<strong>an</strong>ce may not always be thebest predictor of which species are adversely affected by disturb<strong>an</strong>ce(Gill <strong><strong>an</strong>d</strong> Sutherl<strong><strong>an</strong>d</strong>, 2000; Gill et al., 2001). Forexample, species that do not exhibit strong behavioral avoid<strong>an</strong>ceof hum<strong>an</strong>s, such as mule deer <strong>in</strong> this study, may stillsuffer fitness impacts if the costs of mov<strong>in</strong>g to avoid hum<strong>an</strong>recreation are overly high. Conversely, although we expectspatial <strong><strong>an</strong>d</strong> temporal displacement by bobcats <strong><strong>an</strong>d</strong> coyotesto hum<strong>an</strong> recreation to be associated with real costs <strong>in</strong> termsof energetic losses or <strong>in</strong>creased stress levels, more research isnecessary to determ<strong>in</strong>e how such avoid<strong>an</strong>ce actually tr<strong>an</strong>slates<strong>in</strong>to ch<strong>an</strong>ges <strong>in</strong> survival, reproduction, <strong><strong>an</strong>d</strong> ultimatelypopulation persistence.AcknowledgementsWe th<strong>an</strong>k the Nature Reserve of Or<strong>an</strong>ge County, The NatureConserv<strong>an</strong>cy <strong><strong>an</strong>d</strong> The Irv<strong>in</strong>e Comp<strong>an</strong>y for their generousfund<strong>in</strong>g <strong><strong>an</strong>d</strong> support. This project could not have been completedwithout the cont<strong>in</strong>uous assist<strong>an</strong>ce from TNC-Irv<strong>in</strong>epersonnel: T. Smith, M. Erv<strong>in</strong> <strong><strong>an</strong>d</strong> D. Clarke. Special th<strong>an</strong>ksto all those who assisted <strong>in</strong> fieldwork: K. Raymond, G. Geye,L. C<strong>an</strong>ny, J. Cook, F.E. Askew <strong><strong>an</strong>d</strong> R. Lemonds. We th<strong>an</strong>k C. Ribic<strong><strong>an</strong>d</strong> D. Field of the University of Wiscons<strong>in</strong>-Madison whoprovided valuable advice <strong><strong>an</strong>d</strong> support, <strong><strong>an</strong>d</strong> <strong>an</strong>onymousreviewers for their extremely helpful comments <strong><strong>an</strong>d</strong>suggestions.REFERENCESAaris-Sorensen, J., 1987. Past <strong><strong>an</strong>d</strong> present distribution of badgersMeles meles <strong>in</strong> the Copenhagen area. 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