ZOOLOGICAL RESEARCH A road for a promising future for China’s primates: The potential for restoration ColinA.Chapman1,2,3,* 1DepartmentofAnthropology,McGillUniversity,MontréalQuébecH3A2T7,Canada 2WildlifeConservationSociety,BronxNewYork 10460,USA 3SectionofSocialSystemsEvolution,PrimateResearchInstitute,KyotoUniversity,Inuyama484-8506,Japan ABSTRACT waslostgloballyandinthetropicsforestlossincreasedeach China is one of the most dynamic countries of year (Hansen et al., 2013). To put this in perspective, this areaisapproximatelythesizeofMexico. Globalestimatesof the world and it shelters some amazing levels of theextentofwildlifeover-exploitationareverypoor. However, biodiversity, including some very special primate Bennettetal. (2000)estimatedthatsixmillionmammalswere species. However, primarily as a result of forest huntedannuallyinMalaysianBorneo. Withrespecttoclimate loss, most of which occurred in historical times, change, temperatures are predicted to increase by 1.5 ◦C by approximately 70% of China’s primate species have theendofthe21stcentury(IPCC,2014)andusingmoderate greenhouse gas emission estimates, it is projected that by less than 3 000 individuals. Here I evaluate one 210075%ofalltropicalforestspresentin2000willexperience road for future conservation/development that could temperatures that are higher than the temperatures presently produce very positive gains for China’s primates; supportingclosedcanopyforests(Peresetal.,2016;Wrightet namelyforestrestoration. Iarguethatforalargescale al.,2009). restorationprojecttobepossibletwoconditionsmust China follows some of these patterns, but many aspects be met; the right societal conditions must exist and how China has changed are unique; they represent different challenges and most importantly different opportunities. For therightknowledgemustbeinhand. Thisevaluation example, since 2000, China’s Gross Domestic Product has suggeststhattherestorationofnativeforesttosupport increasedbyapproximately270%andChinaisnowtheworld’s many of China’s primates holds great potential to largesteconomy(Ahrendsetal.,2017). Theeconomyhasto advanceconservationgoalsandtopromoteprimate support a population approaching 1.4 billion people (Deng et populationrecovery. al.,2015;Wei&Ye,2014). Boththeeconomicandpopulation growthhavecomeatanenvironmentalcost.Itisestimatedthat Keywords: Conservation; Forest restoration; Chinahaslostbetween1.9and2.7millionkm2 ofitsoriginal Regeneration;Primatepopulationdynamics forest in the last 2 000 years (based on models of habitat suitability;Ahrendsetal.,2017);thisisanareaapproximately INTRODUCTION the size of the Democratic Republic of Congo. This has cost China in terms of primate diversity and population size. At The world is changing rapidly and China represents one of leastthreespecieshavebeenextirpatedfromChina(Pygathrix the most dynamic countries on earth and it shelters some nemaeus,Hylobateslaryunnanensis,Nomascusleucogenys) amazinglevelsofbiodiversity(i.e.,>30000speciesofvascular plants (behind only Brazil and Colombia), ~2 340 species of terrestrialvertebrates(Liuetal.,2003)). Globally, biodiversity is being lost at an accelerating rate, with current extinction Received:31October2017;Accepted:25December2017;Online:09 ratesapproximately1000timeshigherthanbackgroundrates March2018 (Pimmetal.,2014). Recentestimatessuggestthat11000–58 Foundationitems:SupportedbytheCanadaResearchChairsProgram, 000 species are lost each year and that surviving vertebrate theNaturalScienceandEngineeringResearchCouncilofCanada,and species have declined in abundance by 25% since 1970 (Dirzo et al., 2014). Humans are clearly responsible for this KyotoUniversity acceleratinglossofbiodiversity,includingtheendangermentof *Correspondingauthor,E-mail:[email protected] primates. Between 2000 and 2012, 2.3 million km2 of forest DOI:10.24272/j.issn.2095-8137.2018.032 244 SciencePress ZoologicalResearch39(4):244–248,2018 and the Hainan (Nomascus hainanus) and Cao-vit gibbons than2500reservescovering1.6millionkm2(thisareaincludes (Nomascusnasutus)willalmostcertainlynotseetheturnofthe 17.1%ofthecountry,whichisapproximatelythesizeofIranor century without very effective conservation action (Fan, 2017; twice the state of Texas). Lastly, over the last two decades Turvey et al., 2017). Gibbons were once found from Xi’an in there has been a large movement of people from rural areas central China east to Shanghai and all the way south to the (i.e.,nexttothereserveswhereChina’sprimatesarefound)to border(Fan,2017; Turveyetal.,2017; Zhou&Zhang,2013); thecities.Infact,theurbanizationraterosefrom17.9to52.6% now they are isolated in a few forest fragments to the south. between1978and2012andcurrentlymorethanhalfofChina’s Even orangutans were found in southern China only 12 500 populationliveincities(Dengetal.,2015). yearsago(Hussonetal.,2009;Steiper,2006),buttheyareno Intermsoftherightsocietalconditionstomakerestoration longerfoundonmainlandAsia. Arecentanalysisconsidering possible, an area still requiring a great deal of effort is 22 of the 27 primate species in China (Fan & Ma, 2018) that of hunting. In many areas of southern China, where suggeststhat15ofthespecieshavelessthan3000individuals forest cover is still substantial, primate populations can be and that 81% of the populations of all Chinese primates are dramatically reduced because of hunting (Harrison et al., declining(Estradaetal.,2017).Thesesortsofstatisticsclearly 2016). Even though some primates have Class I Protected indicatethatChinahaslostagreatdealofgroundinthebattle AnimalsintheChineseWildlifeConservationLawandhunting to conserve its biodiversity, but they also illustrate that China gunshavebeenoutlawedandconfiscated, illegalhuntingstill hasgreatpotentialintermsofprimateconservation. frequently occurs as it has been a traditional practise that is Theobjectiveofthisopinionarticleforthisspecialissueon promoted by poverty in local communities, the use of wildlife Primates and Primatology in China is to evaluate one road for medicinal uses, and poor knowledge and enforcement of for future conservation/development that could produce very the laws (Fan et al., 2014). For example, in south-west positive gains for China’s primates; namely forest restoration. Guangxi Province, Francois’ langur (Trachypithecus francoisi) There is clearly the need for restoration, as many of China’s populations declined by 90% between the early 1980s and primates are only found in small isolated forests; thus early 2000s, at which time the total population size was expanding their habitat and connecting fragments is clearly estimated to be only approximately 300 individuals found in vitallyneeded. 14isolatedpopulations. Theresearchersconductingthelater survey concluded that the primary threat to the langur was MAKING RESTORATION A VIABLE CONSERVATION hunting,primarilyfortraditionalmedicine(Lietal.,2007). STRATEGY The second requirement is that the knowledge must be available to effectively carry out a large restoration projects. For a large scale restoration project to be possible two Globally,thereareonlyahandfulofstudiesabouttheresponse conditions must be met. First, there must be the right ofprimatecommunitiestoforestregeneration;however,these societal conditions to make restoration possible and second studies suggest that forests, and the primate community they the knowledge must be in hand to carry out such projects. support, can rebound very rapidly when left to recover or In terms of the societal conditions, it appears that the encouraged to recover. For example, Baya & Storch (2010) timing is right for restoration projects. In November 1988, surveyed a site in Korup National Park, Cameroon that was government of China enacted the "Law of the People’s abandoned 7–8 years previously and found populations of all Republic of China on the Protection of Wildlife" to facilitate eight species of diurnal primates that occur in the region; in the protection and management of wildlife. This law is addition, sighting frequency in this recovering area was not the first truly comprehensive law to protect wildlife in China. significantly different from other sectors of the park (Linder, However, since 1998, the Chinese government has enacted 2008). InKibaleNationalPark,Uganda,sevenyearsafteran several national biodiversity conservation regulations, such areaofgrasslandwasreplantedwithtreesaspartofacarbon as the Natural Forest Protection Project and Ecological offset program (Omeja et al., 2012), all species of diurnal ForestCompensation, whichhavebeeneffectiveinimproving primateswerepresentinhighnumbers,includingendangered environmentalconditionsinmanyareas(Renetal.,2015;Xuet redcolobusand chimpanzee. Suchstudies givehopeforthe al.,2009). Governmentfinancingforprotectedareashasalso future. increasedfollowingthelaunchoftheWildlifeConservationand WithinChinaagreatdealofresearchhasaccumulatedover NatureReserveConstructionProjectandtheSpecialFundfor the last two or so decades that provides exactly the type of CapacityBuildingofNational-LevelNatureReserves. Chinais informationneededforrestoration/conservationefforts.Tostart investingsubstantiallyinreforestationandtreeplantingefforts such efforts accurate information on the state of the species and this has totalled more than US$ 100 billion in the past to be targeted must be known. There is extensive survey decade alone (Ahrends et al., 2017; Li et al., 2013; Viña information on the current size and threats to the country’s et al., 2016; Zhang et al., 2000; Zhang, 2015). China now primates (e.g., Chen et al., 2015; Cui et al., 2016). The has theworld’s largestplantation area(approx. 800000 km2 synthesis of this information will be vital in determining the (approximatelythesizeofMozambique,Ahrendsetal.,2017). locationstobeprioritizedinrestorationefforts;however,other Atthesametime,Chinaistryingtoreducepressuresonnatural localaspects,suchasthewillingnessofthelocalpopulationto foreststhroughstrictbansonlogginginprimaryforestsanda participate in restoration and to not hunt primates must also massiveexpansionofitsforestreservestoacurrenttotalmore ZoologicalResearch39(4):244–248,2018 245 be considered. Next, information must be available on the reforestationeffortsonaverylargescale. habitat requirements of the species targeted for help from a CONCLUSION forest restoration project and again, there are many detailed projects focusing on primate habitat use (Fan et al., 2009, Primatesareverycharismaticandaregenerallylikedbyboth 2012; Guo et al., 2008; Li & Rogers, 2006; Liu et al., 2013). theChinesepeopleandinternationalgroups,thustheycanact Of particular importance if the restorationproject is to involve as“Flagship”or“GuardianAngel”speciestopromotethevalue activereplantingoftreesisdetailedinformationonthedietof of restoring these lands to a native forest (Bicca-Marques & the primates. With this information, either the food trees of De Freitas, 2010; Simberloff, 1998). It is my opinion that this theanimalscanbeplanted, orspecieswithsimilarnutritional is an exciting time to integrate restoration into conservation traitscanbeusedintherestorationeffort. Therehavebeena strategies to make informed and effective conservation and numberofhighqualitystudiesdoneonthenutritionalecology managementdecisionsfortheprimatesofChina. ofChina’sprimates(e.g.,Liuetal.,2013;Maetal.,2017;Hou et al., 2018). To make restorations efforts more effective, it COMPETINGINTERESTS is critical to understand the severity and geographical nature of threats to primates in China other than habitat loss (e.g., Theauthorsdeclarethattheyhavenocompetinginterests. live capture for trade, bushmeat, and tourism; Li et al., 2003; AUTHORS’CONTRIBUTIONS Xia et al., 2016; Yang et al., 2007; Zhu et al., 2013). In addition, information on conservation genetics is needed to C.C.investigatedandwrotethemanuscript, buthebenefitedfromtalking determine the nature of corridors that can allow population tomanyfriendsandcolleaguesatthe2017ChinaPrimatologicalSocietyin mixing(Liuetal.,2015).Withrespecttoconservationgenetics, Xi’an. information concerning past interpopulational gene flow and landscape barriers on both short (e.g., satellite and aerial ACKNOWLEDGEMENTS photography)andlongtimeframes(e.g., riverbarriers), while rare (but see Wang et al., 2017), will be particularly valuable IwouldliketothankRongHouandPeng-FeiFanforhelpfulcommentson indeterminingthedispersalcapabilitiesofprimatesrelativeto themanuscript. differenttypesofbarriersandcanbeusedtoprovideguidance REFERENCES astothenatureofcorridorsthatcanbeconstructedtofacilitate populationmixing(Guoetal.,2010;Wangetal.,2015,2017). AhrendsA,HollingsworthPM,BeckschäferP,ChenHF,ZomerRJ,ZhangLB, WangMC,XuJC.2017.China’sfighttohalttreecoverloss.Proceedingsof WHAT REMAINS TO BE DONE FOR RESTORATION IN CHINA theRoyalSocietyB:BiologicalSciences,284(1854):20162559. Baya L, Storch I. 2010. Status of diurnal primate populations at the While this existing information is extremely valuable, what formersettlementofadisplacedvillageinCameroon.AmericanJournalof is lacking is data specific to restoration efforts and studies Primatology,72(7):645–652. documenting behavioral patterns and responses of primates Bennett EL, Nyaoi A, Sompud J. 2000. Saving Borneo’s bacon: the to the regeneration of forests. For restoration projects to be sustainabilityofhuntinginSarawakandSabah.In:RobinsonJG,BennettEL. most effective, information on the survival strategies used in HuntingforSustainabilityinTropicalForests.NewYork:ColumbiaUniversity regeneratingforestsofallthemajorprimategroups,including Press,305–324. prosimians, macaques, colobines, and gibbons will be vital. While this is a formidable task, it also represents an exciting Bicca-MarquesJC,DeFreitasDS.2010.Theroleofmonkeys,mosquitoes, challengetoacademicsandUniversities;onewherethevalue andhumansintheoccurrenceofayellowfeveroutbreakinafragmented ofresearchcanbeillustratedtothegovernmentandpublic. landscapeinsouthBrazil: protectinghowlermonkeysisamatterofpublic What now remains to be done is to pull this societal health.TropicalConservationScience,3(1):78–89. potential and information together to facilitate large-scale ChenYX,XiangZF,WangXW,XiaoW,XiaoZS,RenBP,HeCX,Sang forest restoration efforts that is critically needed for primate CH,LiHS,LiM.2015.Preliminarystudyofthenewlydiscoveredprimate conservation.SincesomanyprimatespeciesinChinaareonly species Rhinopithecus strykeri at Pianma, Yunnan, China using infrared hanging on as small remnant populations that are often only cameratraps.InternationalJournalofPrimatology,36(4):679–690. composedofafewgroups(e.g.,thecaovitgibbonpopulation CuiLW,LiYC,MaC,ScottMB,LiJF,HeXY,LiDH,SunJ,SunWM,Xiao isestimatedtoonlyinvolve18groupsoccupyingforestpatches W.2016.DistributionandconservationstatusofShortridge’scappedlangurs of only 2 000 hm2 with only 3–4 groups in China (Fan et TrachypithecusshortridgeiinChina.Oryx,50(4):732–741. al.,2011))theonlywaytoeffectivelypromoteconservationof Deng XZ, Huang JK, Rozelle S, Zhang JP, Li ZH. 2015. Impact of theseprimatesinthewildisthroughrestoration.Thiswilllikely requiresomesortofwellfinancedcoordinatingagencythatis urbanizationoncultivatedlandchangesinChina.LandUsePolicy,45:1–7. able to rally national and international scholars, conservation Dirzo R, Young HS, Galetti M, Ceballos G, Isaac NJB, Collen B. 2014. organizations, government agencies, and the public to first DefaunationintheAnthropocene.Science,345(6195):401–406. provided the needed scientific information and then to use EstradaA,GarberPA,RylandsAB,RoosC,Fernandez-DuqueE,DiFiore this information to promote both natural regeneration and A, Nekaris KAI, Nijman V, Heymann EW, Lambert JE, Rovero F, Barelli 246 www.zoores.ac.cn C,SetchellJM,GillespieTR,MittermeierRA,ArregoitiaLV,deGuineaM, François’langurTrachypithecusfrancoisiinGuangxiProvince,China.Oryx, Gouveia S, Dobrovolski R, Shanee S, Shanee N, Boyle SA, Fuentes A, 41(1):38–43. MacKinnon KC, Amato KR, Meyer ALS, Wich S, Sussman RW, Pan RL, LiYB,LiWJ,ZhangCC,FanMM.2013.Currentstatusandrecenttrendsin KoneI,LiBG.2017.Impendingextinctioncrisisoftheworld’sprimates:why financingChina’snaturereserves.BiologicalConservation,158:296–300. primatesmatter.ScienceAdvances,3(1):e1600946. LiZY,RogersME.2006.Fooditemsconsumedbywhite-headedlangursin Fan PF, Ma C. 2018. Extant primates and development of primatology in Fusui,China.InternationalJournalofPrimatology,27(6):1551–1567. China: publications, student training, and funding. Zoological Research, LinderJM.2008.TheImpactofHuntingonPrimatesinKorupNationalPark, 39(4):249–254. Cameroon: Implications for Primate Conservation. Ph.D. thesis. The City FanPF,NiQY,SunGZ,HuangB,JiangXL.2009.Gibbonsunderseasonal UniversityofNewYork,NewYork,376. stress: the diet of the black crested gibbon (Nomascus concolor) on Mt. LiuJG,OuyangZY,PimmSL,RavenPH,WangXK,MiaoH,HanNY.2003. Wuliang,CentralYunnan,China.Primates,50(1):37–44. ProtectingChina’sbiodiversity.Science,300(5623):1240–1241. FanPF,FeiHL,ScottMB,ZhangW,MaCY.2011.Habitatandfoodchoice Liu XC, Stanford CB, Yang JY, Yao H, Li YM. 2013. Foods Eaten by of the critically endangered cao vit gibbon (Nomascus nasutus) in China: theSichuansnub-nosedmonkey(Rhinopithecusroxellana)inShennongjia implicationsforconservation.BiologicalConservation,144(9):2247–2254. nationalnaturereserve,China,inrelationtonutritionalchemistry.American Fan PF, Fei HL, Ma CY. 2012. Behavioral responses of cao vit gibbon JournalofPrimatology,75(8):860–871. (Nomascus nasutus) to variations in food abundance and temperature in LiuZJ,LiuGJ,RoosC,WangZM,XiangZF,ZhuPF,WangBS,RenBP,Shi Bangliang,Jingxi,China.AmericanJournalofPrimatology,74(7):632–641. FL,PanHJ,LiM.2015.Implicationsofgeneticsandcurrentprotectedareas Fan PF, Fei HL, Luo AD. 2014. Ecological extinction of the Critically forconservationof5endangeredprimatesinChina.ConservationBiology, Endangerednorthernwhite-cheekedgibbonNomascusleucogenysinChina. 29(6):1508–1517. Oryx,48(1):52–55. Ma CY, Liao JC, Fan PF. 2017. Food selection in relation to nutritional FanPF.2017.Thepast,present,andfutureofgibbonsinChina.Biological chemistryofCaoVitgibbonsinJingxi,China.Primates,58(1):63–74. Conservation,210:29–39. OmejaPA,ObuaJ,RwetsibaA,ChapmanCA.2012.Biomassaccumulation Guo ST, Ji WH, Li BG, Li M. 2008. Response of a group of Sichuan in tropical lands with different disturbance histories: contrasts within one snub-nosedmonkeystocommercialloggingintheQinlingMountains,China. landscape and across regions. Forest Ecology and Management, 269: ConservationBiology,22(4):1055–1064. 293–300. GuoST,JiWH,LiM,ChangHL,LiBG.2010.Thematingsystemofthe Peres CA, Emilio T, Schietti J, Desmoulière SJ, Levi T. 2016. Dispersal Sichuansnub-nosedmonkey(Rhinopithecusroxellana).AmericanJournal limitation induces long-term biomass collapse in overhunted Amazonian ofPrimatology,72(1):25–32. forests. Proceedings of the National Academy of Sciences of the United HansenMC,PotapovPV,MooreR,HancherM,TurubanovaSA,Tyukavina StatesofAmerica,113(4):892–897. A,ThauD,StehmanSV,GoetzSJ,LovelandTR,KommareddyA,EgorovA, PimmSL,JenkinsCN,AbellR,BrooksTM,GittlemanJL,JoppaLN,Raven ChiniL,JusticeCO,TownshendJRG.2013.High-resolutionglobalmapsof PH,RobertsCM,SextonJO.2014.Thebiodiversityofspeciesandtheirrates 21st-centuryforestcoverchange.Science,342(6160):850–853. ofextinction,distribution,andprotection.Science,344(6187):1246752. Harrison RD, Sreekar R, Brodie JF, Brook S, Luskin M, O’Kelly H, Rao RenGP,YoungSS,WangL,WangW,LongYC,WuRD,LiJS,ZhuJG,Yu M, Scheffers B, Velho N. 2016. Impacts of hunting on tropical forests in DW.2015.EffectivenessofChina’snationalforestprotectionprogramand SoutheastAsia.ConservationBiology,30(5):972–981. naturereserves.ConservationBiology,29(5):1368–1377. Hou R, Chapman CA, Garber PA, Guo S, Li B. 2018. Dietary and SimberloffD.1998.Flagships,umbrellas,andkeystones: issingle-species nutritional adaptions to extremes of northern-living by Rhinopithecus managementpasséinthelandscapeera? BiologicalConservation,83(3): roxellana.AmericanJournalofPrimatology.(inpress) 247–257. Husson SJ, Wich SA, Marshall AJ, Dennis RD, Ancrenaz M, Brassey R, Steiper ME. 2006. Population history, biogeography, and taxonomy of GumalM,HearnAJ,MeijaardE,SimorangkirT,SingletonI.2009.Orangutan orangutans(Genus: Pongo)basedonapopulationgeneticmeta-analysis distribution, density, abundanceandimpactsofdisturbance.In: WichSA, ofmultipleloci.JournalofHumanEvolution,50(5):509–522. AtmokoSSU,SetiaTM,VanSchaikCP.Orangutans: GeographicVariation TurveyST,BryantJV,DuncanC,WongMHG,GuanZH,FeiHL,MaCY,Hong inBehavioralEcologyandConservation.Oxford: OxfordUniversityPress, XJ,NashHC,ChanBPL,XuY,FanPF.2017.Howmanyremnantgibbon 77–96. populationsareleftonHainan?Testingtheuseoflocalecologicalknowledge IPCC.2014.Climatechange2014:synthesisreport.Contributionofworking to detect cryptic threatened primates. American Journal of Primatology, groupsI,IIandIIItothefifthassessmentreportoftheintergovernmental 79(2):e22593. panelonclimatechange.In: CoreWritingTeam,PachauriRK,MeyerLA. ViñaA,McConnellWJ,YangHB,XuZC,LiuJG.2016.Effectsofconservation Geneva,Switzerland:IPCC. policyonChina’sforestrecovery.ScienceAdvances,2(3):e1500965. Li BG, Jia ZY, Pan RL, Ren BP. 2003. Changes in distribution of the Wang W, Qiao Y, Li S, Pan W, Yao M. 2017. Low genetic diversity and snub-nosedmonkeyinChina.In:MarshLK.PrimatesinFragments:Ecology strongpopulationstructureshapedbyanthropogenichabitatfragmentation andConservation.NewYork:Springer,29–51. inacriticallyendangeredprimate,Trachypithecusleucocephalus.Heredity, Li YB, Huang CM, Ding P, Tang Z, Wood C. 2007. Dramatic decline of 118(6):542–553. ZoologicalResearch39(4):244–248,2018 247 WangWR,QiaoY,PanWS,YaoM.2015.Lowgeneticdiversityandstrong YangDD,DaiXF,DengYP,LuWQ,JiangZG.2007.Changesinattitudes geographical structure of the critically endangered white-headed langur towardwildlifeandwildlifemeatsinHunanProvince,centralChina,before (Trachypithecus leucocephalus) inferred from mitochondrial DNA control and after the severe acute respiratory syndrome outbreak. Integrative regionsequences.PLoSOne,10(6):e0129782. Zoology,2(1):19–25. WeiYD,YeXY.2014.Urbanization,urbanlandexpansionandenvironmental ZhangL.2015.Specialsection:balancingconservationanddevelopmentto changeinChina.Stochasticenvironmentalresearchandriskassessment, preserveChina’sbiodiversity.ConservationBiology,29(6):1496. 28(4):757–765. ZhangPC,ShaoGF,ZhaoG,LeMasterDC,ParkerGR,DunningJrJB, Wright SJ, Muller-Landau HC, Schipper J. 2009. The future of tropical LiQL.2000.China’sforestpolicyforthe21stcentury.Science,288(5474): speciesonawarmerplanet.ConservationBiology,23(6):1418–1426. 2135–2136. XiaW,RenB,LiY,HuJ,HeX,KrztonA,LiM,LiD.2016.Behavioural Zhou YH, Zhang P. 2013. Distribution and vicissitude of gibbons responsesofYunnansnub-nosedmonkeys(Rhinopithecusbieti)totourists (Hylobatidae)inChinaduringthelast500years.ActaTheriologicaSinica, in a provisioned monkey group in Baimaxueshan Nature Reserve. Folia 33(3):258–266.(inChinese) Primatologica,87(6):349–360. ZhuY,LiJH,XiaDP,SunBH,XuYR,WangX,ZhangD.2013.Potential XuHG,TangXP,LiuJY,DingH,WuJ,ZhangM,YangQW,CaiL,ZhaoHJ, pathogentransmissionriskinnon-humanprimateecotourism:acasestudy LiuY.2009.China’sprogresstowardthesignificantreductionoftherateof atMt.Huangshan,China.LifeScienceJournal,10(1):2754–2759. biodiversityloss.BioScience,59(10):843–852. 248 www.zoores.ac.cn