protected areas, conservation stakeholders and the naturalization of southern europe
TRANSCRIPT
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Title:
ProtectedAreas,ConservationStakeholdersand the ‘Naturalization’
ofSouthernEurope
Author:
JoseA.CORTES‐VAZQUEZDisciplineofGeography,SchoolofGeographyandArchaeology,NationalUniversityofIrelandGalway,Galway,[email protected]:10.247
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Abstract:
The critical analysis of conservation conflicts in Protected Areas (PAs) raises
interestingquestionsabouttheredefinitionofhuman‐environmentrelations in
thecurrentecologicalcrisis.Inrecentyearsthesedebateshaveunveiledthat,in
theattempttodefinethe‘proper’placeofhumansinnature,PAshaveembodied
moderndualisticworldviews,whichunderstandnatureasarealmdifferentfrom
society, culture and ’civilisation’. In this paper, I suggest that the utilisation of
theseworldviewsshouldbeunderstoodaspartoftheconceptualapparatusthat
enablesatransitioninmanagementrolesinProtectedAreas,throughwhichnew
empoweredgroupsaregrantedtherighttocontrolandusenaturalresources.By
analysingthepracticesanddiscoursesofconservationstakeholdersattheCabo
de Gata‐Níjar Natural Park, in southern Spain, I show that modern ideas of
nature are essential to the collective appropriation of Cabo de Gata by new
empowered groups because these ideas justify a new way of managing local
resourcesinaccordancewiththeirowninterestsanddesires.Iconcludethatthis
has deep implications for the study of people‐park conflicts and the problems
associatedtothepromotionofmoreenvironmentallyfriendlywaysofmastering
theenvironment,whichmustbeapproachedinthelightofthepowerrelations
associated to the appropriation of territory and natural resources. I also
conclude that, in order to understand how the nature‐society dualism still
dictates the way we should relate to the environment, we must trace the
practices of those who bear this worldview and unveil the strategies and
mechanismsthatareused.
Keywords
Protected Areas, Conservation Policies, Ecotourism, Nature/Society, Europe,
ConservationStakeholders
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Introduction
Central to the constitution of current ecological crises are modernist
environmentalviewsthatseparatenaturefromsocietyandwhichmakepossible
large‐scale exploitation and despoliation of natural resources (Latour 1993,
Arnold 1996). This ontological separation is also integral to the emergence of
modern environmentalism and many attempts to redress the ecological
problems caused by capitalism (Pepper 1996). The tensions surrounding this
separationandattemptstodealwiththemarevisibleinnumerousconservation
conflicts, fromdisputesbetweenbiodiversityconservationand farming, fishing
andgrazingpracticestothematerialandsymbolicevictionoflocalgroupsfrom
conservation‐targeted areas (Redpath et al 2013). Critiques of these conflicts
contend that, despite promoting new environmental attitudes, most
conservation initiatives have failed to question the nature‐society separation
inherenttoecologicallydepredatoryinitiatives.
Critical Social Sciences studying conflicts in Protected Areas (PAs) have
producedespeciallyincisiveanalysesofthelinksbetweenconservationpolicies
andthenature‐societydualism(Westetal2006).Theyareindebtedtothequery
of the US National Park model and its connection to a Western rhetoric of
wilderness,authenticityanduntouchednature(Cronon1995),whichhaslargely
inspiredaState‐centredconservationmodel inmanyother countries inAfrica,
Asia and Latin America (Adams 2004). This model hinges on the coercive
utilisation of State’s force and technologies of governance upon some social
groups in order to create ‘islands’ of supposedly untouched nature; its most
extrememanifestationsbeingtermed‘fortressconservation’(Brockington2002,
Igoe2004).
Although this model has had a limited impact on the design of PAs in other
regionssuchasWesternEurope,wherelocalinhabitants’presenceandinterests
aretoacertainextentacknowledgedinconservationplans(Redford2011),their
critical examination reveals that, in the attempt to define the ‘proper’ place of
humansinnature,thesePAshavealsoembodieddualisticenvironmentalviews.
DrawingonanontologynamedbyDescola (2005) ‘WesternNaturalism’, these
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conservation policies have incorporated ideas of nature and society in binary
opposition, extending the belief that conservation depends a great deal on
limitingthetransformationofnaturalresourcesbyhumans(Santamarina2009).
The counterintuive utilisation of these ideas of nature in areas broadly
accreditedashighlytransformedandshapedbyhumanbeings,suchasthosein
the European Mediterranean Basin (Grove and Rackham 2001), converts
European Protected Areas in unique places for the study of how Western
naturalismisstrategicallyutilisedwithintheconceptualapparatusthatjustifies
theintroductionofconservationpolicies.
Thispaperseekstomakeacontributiontothisfieldbyfocusingonkeymembers
of the network of actors that support conservation policies in European PAs.
Through the study of their situated interests, intentions, practices and
environmentaldiscourses,myanalysis engageswith twomainbodiesofwork.
The first is the study of the drivers of conservation policies and development
initiatives,whosenarrativesareusuallyportrayedasapoliticalintheprocessof
decision‐making(Ferguson1990,Escobar1998,Robbins2004,Peetetal2010)
andassociateddebatesabouttheroleofscientists,economiclobbiesandexpert
bureaucracies in policies of environmental governance (Scott 1998, Jasanoff
2004, Brockington and Duffy 2010). The second is the study of Western
naturalism(Descola2005)andthequestioningithasbeensubjectedtoinrecent
decades (Haraway 1988, Latour 1993, Castree and Braun 2001, Whatmore
2001).Inparticular,Iengagewithongoingdebatesthatqueryifnaturalismcan
become an empirical object of study for ethnographers, which would involve
studying those who bear and enact this particular ontology (Candea and
Alcayna‐Stevens2012).
Myanalysiscentresonaparticularcase:theCabodeGata‐NíjarNaturalPark,in
the Region of Andalusia, southern Spain. The story of conservation in this
extremelydry, coastalplace featuresdecade‐long socialdisputes regarding the
introduction of a more environmentally friendly way of managing natural
resources,whichhas tried to hamper the expansionofmass tourism, industry
and intense irrigated agriculture and to redress the ecological impact of non‐
intensive, customary practices, such as fishing, grazing and dry farming. I
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examine thekeyrole thatcertain local stakeholdersplayed in thisprocessand
howmodern ideas of nature were utilised to transform Cabo de Gata from a
historical farming, grazing and fishing area to a biodiversity reserve and
ecotourismdestination.ForreasonsthatIwillexplaininduecourse,myanalysis
willcentreontwospecificgroups:scientistsandnewex‐urbaninhabitants.
My examination of the Cabo de Gata‐Níjar Natural Park draws on a growing
literature about the links between the nature‐society dualism, people‐park
conflicts and issues of territorial reintegration and land‐use reorganisation
across Europe (Green 2005, Vaccaro and Beltran 2008, Ruiz et al 2009,
Santamarina2009,Valcuendeetal2011,Cortes‐Vazquez2012).Forexample,in
AndalusiatheestablishmentofnewPAsinthelastquarterofacentury,covering
up to twenty per cent of the territory, has paralleled the promotion of new
economic practices based onWestern rhetoric of wilderness, authenticity and
untouchednature,mainlyecotourism(Escalera2011).Thishasintroducedland‐
use changes not only informed by environmentalist concerns but also by EU
macroeconomic interests, which aim to promote the growth of a service
economywithineconomicallymarginalareas,replacingcustomaryfarmingand
fishing practices whose reliance on subsidies makes them clearly deficient
withinaglobalisedeconomy(Gonzalez1993,Coca2008).
In order to conceptualise similar processes of ecological redefinition,
environmentalgovernanceandland‐usereorganisationandtheirconnectionto
the actions and interests of empowered groups, usually with an urban
background, some scholars have proposed such terms as ‘re‐territorialisation’
(VaccaroandBeltran2008)and ‘heritagisation’ (FrigoléandDelMarmol2009,
Quintero2009).Moreorlessexplicitly,thesetermshingeonanapproachtothe
idea of territory as an area that a particular group claim to be of their own,
grantingsomeofitsmembersthecontrolandmanagementofnaturalresources
(cf.Godelier1986).Withasimilarrationale,Iwillrefertotheissuesanalysedin
thispaperusingtheterm‘naturalization’1foritstressestheessentialroleofthe
1There isan important issuehere, identifiedbyonereaderofanearlierversionof thispaper.The word ‘naturalization’ has other meanings, some of them much more popular, which cangenerate some confusion. The Oxford Dictionary defines the term naturalize, from whichnaturalization derives, as 1) admitting (a foreigner) to the citizenship of a country; 2)
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ideaofnatureinjustifyingtheintroductionofconservationpolicies,whichIwill
approachasthecollectiveappropriationofaterritoryanditsresourcesbynew
empoweredgroups2.
ThispaperstartswithahistoricalreviewoftheCabodeGata‐NíjarNaturalPark.
I will describe the collaborations in which scientists and new ex‐urban
inhabitantsengagedinsupportoftheestablishmentofthisNaturalParkduring
the1970sand1980s.Iwillthenanalysetheconceptualapparatusthatunderlies
thediscoursestheseconservationstakeholdershaveenacted;discourseswhose
aim is both to justify their support and to delegitimize those that oppose
conservationplansinCabodeGata.Iwillparticularlyemphasisetheirstrategic
utilisationofthenature‐societydualismamidstnotionsof livelihood,valueand
land‐use rights. Finally, Iwill show the extent the Park policy embodies these
interestsandenvironmentalnarratives.
Thisanalysiswillpermitmetoreflectabouttheimpactsconservationinitiatives
haveonvastareasacrossEuropeandtheinfluenceofcertainideasofnaturein
thematerial and symbolic reshaping of these territories. This will allow for a
more empirically‐based examination of the political dimensions of modernist
ideasofnature,theintimaciesbetweentheseideasandcertaininterestsandthe
challenges this poses to the ethnographic study of people‐park conflicts,when
establishing(aplantoranimal)sothatitliveswildinaregionwhereitisnotindigenous;and3)regardingasorcausingtoappearnaturalandexplaining(aphenomenon)inanaturalisticway.Althoughthemainstreamuseofthetermregardsthefirstdefinition,theothertwomeaningsarecloselyrelatedtothemainsubjectofthispaper.Despitetheconfusionthatthismightgenerate,thereasonforusingthetermnaturalizationconcerns itsexplanatorypower. Ibelievethetermsummarisestheprocessofmaterialandsymbolicproductionofaspaceinaccordancewiththeparticular environmental views that are inherent to Western Naturalism, which is the mainphenomenon I study here. As such, I defend that the term is a much more precise of theparticularities affecting Natural Protected Areas than those more general ones, including re‐territorialisation and heritagisation. Whether there might be connections between thisphenomenonandotherscoveredby the termNaturalization, it isbynomeansmy intention toexploretheminthispaper.2ThisreflectsthelargeextentmyanalysisisinfluencedbyFoucauldianandMarxianapproachestothesociety‐environmentnexusandtheproductionofnature(Castree2000,2002)aswellasby related analysis about the links between conservation policies and the distribution ofprivilege,fortuneandmisfortune(AndersonandBerglund2003,Brockingtonetal2008).
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we approach themas conflicts over the control of certain territories and their
naturalresources3.
TheBirthofaNaturalPark
TheCabodeGata‐NíjarNaturalParkisa495‐km2coastalprotectedarealocated
within one of the driest regions in Western Europe. A long history of scarce
rainfalls,erosionandresourcemisusehasgeneratedextremelypoorsoilsinthe
area.Todateonlyanimalandplantspeciesfullyadaptedtoitsdesertconditions
are able to growwild.Barrenplains andhills, characterisedby the absenceof
trees and shrub, dominate the landscape. These are interspersed with small
farming fields,wherewheatandbarleyaregrown for the feedingofgoatsand
sheepherds(around300animalsperherd).Theprotectedmarinearea,which
coversalmost25%ofthePark,comprisesasandyseabedwithsmallgroupings
ofseaweedandsomereefs. Ithostsasmallbutdiverse in‐shore fishery that is
exploitedbylocalfishermen.OtheractivitiesintheParkincludeecotourismand
smallinitiativesoffishfarmingandintenseagricultureinplasticpoly‐tunnels.
LikemostruralregionsinAndalusia,overthelasthalfofacenturythisareahas
undergonemajor changes: the 1950s and 1960s agricultural crisis, an intense
de‐agrarianisation process, strong rural‐urban migrations, transformations
linked to the political and economic integration within the EU, interventions
derived from a growing concern about environmental problems and changes
related to the incorporation into global markets (cf. Delgado 2010). These
3ThefindingsIampresentingherearetheresultofasix‐yearresearch,workingwithmembersof theDepartmentofSocialSciencesat thePablodeOlavideUniversity(Spain)ontwoappliedresearch projects involving ethnographic fieldwork in several protected areas in Andalusia,southernSpain(projectreferences:SEJ2004/SOCI‐06161andP06‐RNM‐02139).Icarriedoutmyown research at the Cabo de Gata‐Nijar Natural Park alongside these two projects. Using anethnographic approach based on semi‐structured interviews and participant observation, Ifocused on social conflicts following the introduction of the park’s management and land‐usezoningplan.Ioptedforqualitativedatasincemyintentionwasnottosurveydifferentpositionstowardsconservationinitiatives,buttoobtaina‘thickdescription’–inGeertz’s(1973)terms‐ofthe senses andmeanings given to the changes occurring in Cabo de Gata from the day‐to‐dayexperiences of different groups. For this paper, I am using data gathered via semi‐structuredinterviews and participant observation with Park Managers, scientists, NGO members,ecotourismentrepreneursandothernewexurbaninhabitants,aswellasthoseobtainedfromanin‐depth literature review and the analysis of Park’s conservation plans and other secondaryinformationsources.
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phenomena have deeply influenced Cabo de Gata’s socio‐economic conditions,
moving from decades of deep economic crisis, impoverishment and
marginalisationtoagrowingdependenceofaserviceeconomy,theintervention
ofglobaliseddiscoursesanddisputesoverconflictingdevelopmentstrategies.As
Iwillexplaininthenextfewparagraphs,thesechangesshowdifferentaspectsof
a transition in management roles over natural resources, which at times has
becomearoughanddrawnoutprocess.
IntheearlypartofthetwentiethcenturymostinhabitantsinCabodeGatawere
small landownersandlandlesslabourersthatwereworkinginthelocalmining
industry and in the estatesof just a fewbig andpowerful landowners.Adeep
economic and social crisis was starting to affect this place. Intense mining,
farmingandgrazingactivities in theprevious centurieshad caused severe soil
degradationanddecreasingyields(Sánchez1996).Moreover,thedependenceof
smalllandownersandlandlesspeopleonwagelabour4madethelocaleconomic
situationquicklyworsenfollowingtheendingofbothminingactivitiesandthe
exploitationoflargeplantationsofespartograssintheestatesofbiglandowners.
This crisis alsodraggeddown local in‐shore fishing activities,whichdepended
on the commercialisation of their catches in the nearby farming and mining
towns(Compán1977).Bythe1950sand1960stheareawasalreadyrenowned
asoneofthepoorestandmostmarginalinSpain;farmhouses,villagesandlands
wereprogressivelybeingabandonedasmigrationbecameunavoidableforthose
withfewereconomicresources(Goytisolo2004[1960]).
The1970sand1980sbroughtaboutaseachange.Intenseirrigatedagriculture
underplasticpoly‐tunnelsandmass‐tourismquicklyspreadfromneighbouring
areas,wheretheywerebecomingextremelysuccessful.Populationlevelsbegan
togrow;thearea’seconomicpotentialattractedbothnewinvestorsandsomeof
the people that had emigrated years before (Fernández and Egea 1991)5.
4Thisdependenceonwagelabouristobeunderstoodinrelationtotheprivatisationofcommonlands, which mostly benefited big landowners (Gongora 2004) and which transformed thelivelihoods of most small landowners and landless people, who relied on the utilisation ofcommon lands as a source of fodder, graze and fuel. As Provansal andMolina (1991) analyse,these activities were essential economic complements because of the poor yields that wereobtainedfromagriculture.5Between1900and1970populationleveldecreasedastriking38percent.Thistrendchangedfromthe1980sonwards.Thenumberofpeople living inCabodeGatahasdoubledsince then
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Another extremely important phenomenon was taking place alongside these
changes.AgrowingnumberofpeoplefrombothSpanishandnorthernEuropean
urbanareasstartedtosettledownintheregion.Thestrongurbandevelopment
experiencedinmostcoastalareas inSpaingrantedthebarely inhabited,desert
landscapeofCabodeGatanewmeaningsandvalues.Theseex‐urbaninhabitants
‐mostlyartists,studentsandyoungentrepreneurs‐interpretedtheabandoned
condition of the place in a ‘naturalistic’ way. They felt they had discovered a
‘remote and natural’ space ‐ the ‘ideal’ place to start a new, ‘alternative’ and
‘genuine’lifefarfromthe‘artificiality’ofmodernityandcitylife6.
Furthermore,amuchmorepowerfulphenomenonwasalsotodeeplyimpactthe
region in thoseyears.Followinganationwidepolitical swift that tried to leave
behind the environmentally exploitative policies introduced during the early
Francodictatorshipandtocomecloser toEuropeanpolitical trends, the1970s
and1980switnessedtheestablishmentofmultiplenewProtectedAreasacross
Spain7.Biologists,geologistsandbotanistsplayedakeyroleinthisbyinforming
theselectionof thoseareaswithremarkableecologicalvalues thatwereworth
protecting (Mulero2002). InCabodeGata, these scientists joined thenewex‐
urbaninhabitantsintheirefforttostoptheexpansionofpoly‐tunnelsandmass
tourism,which theybothdeemeda threat to the local ecological andaesthetic
qualities. As a result, a local environmentalist movement emerged, requesting
theintroductionofconservationmeasures(CastroandGuirado1995).Favoured
by this ‘greening’politicalshift, theirdemandswerequicklysuccessfuland the
AndalusiaRegionalGovernmentestablishedtheCabodeGata‐NíjarNaturalPark
in1987.
Thedevelopmentofa‘green’tourismindustrywithintheParkbecameoneofthe
main priorities for policy‐makers,with the aim to provide an environmentally
friendlyeconomicalternative for local inhabitants (Castro1989).However, the
(from 2700 to around 5700) (Source: Andalusia Statistic Institute.http://www.juntadeandalucia.es/institutodeestadisticaycartografia/Lastaccess:July2011).6Similarpopulationmovements,whichVaschetto(2006)terms‘utopianmigrations’,havebeenstudiedinotherpartsoftheWorld,forexampleinSouthAmerica.7Although some conservation initiatives in Spaindateback the early twentieth century, it hasbeen from the 1970s onwards that the number of new PAs increased as never before. InAndalusiatheywerecoveringalmostaquarteroftheterritoryinjustafewyears.
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goal was not only to address concerns about the local populations’ means of
living but also EU macroeconomic interests. The latter were seeking the
promotionof a service economy inmarginal regionsacross theEU inorder to
develop multifunctional rural areas and reduce their dependence on highly
subsidisedfarmingandfishingpractices.Anothercontinent‐wideaffairwasalso
at stake as new Parks were expected to play a part in the territorial
redistribution that sought to compensate exceeding externalities from highly
industrialised and urban areas in central Europe with a protected periphery,
whererecreationalpracticeswerebeingfostered.Asaresult,CabodeGata,like
many other locations across ‘peripheral’ Europe, witnessed a deep land‐use
reorganisation process, led by supra‐local and supra‐national institutionswith
thelocalsupportofincreasinglyempoweredgroupswithanurbanbackground8.
However,mostofthesmall landowners, farmers,shepherdsandfisherfolkthat
still inhabited this areawere reluctant to accept these transformations,whilst
those aspiring to capitalise on irrigated agriculture and mass tourism totally
opposed them. The conservation policy introduced in the area not only
promoted ecotourism but also banned poly‐tunnels, industrial developments
and mass tourism and restricted customary uses in many areas, including
grazing,dryfarmingandin‐shorefishing.Asdiscussedelsewhere(Valcuendeet
al2011,Cortes‐Vazquez2012,Cortes‐VazquezandZedalis2013)atroublesome
relationshipbetweenthesedifferentgroupsandconservationsupporterswasto
condition social life in Cabo de Gata to present times, especially as the Park
mostlyoccupiedprivatelands.
Furthermore, the argument that these farming plots, oldmining areas and in‐
shore fishing grounds were natural areas worth protecting from human
aggression, contradictedwhatmost farmers, shepherds andother local groups
believed tobe the ‘proper’wayofusing local resources in a region they judge
historically poor and ecologically hostile. A closer look at the conservation
measures introduced in the Park will help us understand the source of these
conflictsandtheroleplayedbytheenvironmentalredefinitionthataccompanied8FormoreinformationatEUlevelseeBakeretal(1994).ForspecificdetailsonhowthisaffectedtheframeworkRegionofAndalusia,seeMarchena(1993).SomenotesaboutitsinfluenceinCabodeGatacanbefoundinProvansal(2003).
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thecreationof thisNaturalPark9.Butbeforedoing this,weneed toanalyse in
moredetail the interestsanddesiresof thosesocialgroups thatsupported the
transformation of this historically farming, grazing and fishing area into a
biodiversityreserveandecotourismdestination.
ConservationandLocalStakeholders
As previouslymentioned, in the late 1970s amidst a greeningpolitical context
the SpanishGovernment asked a group of scientists to produce a catalogue of
areas that could be worth protecting within the Almeria Province, where the
NaturalParkislocated.Oneoftheactivitiescarriedoutbythisgroupofexperts‐
mainly geographers, geologists and biologists from different University
DepartmentsandNationalResearchCouncils‐wastostudyCabodeGata’smost
outstanding features: itsvolcanicrocks,rarespeciesof floraand faunaandthe
functioning of its uncommondesert ecosystems. Their intentionwas to assess
the natural value of this region10. Like in many other contexts where expert
knowledge ‐ uncritically portrayed as objective and apolitical (Franklin 1995,
Jasanoff2004)‐hasbeenusedinsupportofpoliticallydrivendecisions(Fairhead
and Leach 1996, 2003), these experts’ research findingswere instrumental to
changing the perception of Cabo de Gata from a barren land to a biodiversity
hotspotandthereforekeytosupportingtheideathatitwasworthprotecting.
Fuelled by these findings, in less than a decade environmentalist ambitions
quickly expanded from theprotectionof only a fewhundred squaremetres of
coastallagoonsin1978toamuchlargerareaalmostthecurrentsizeofthePark
9 Although in this paper I focus exclusively on conservation supporters, I believe furtherclarificationsaboutlocalpopulation’spositionagainsttheParkwouldbewelcome.AsIanalyseelsewhere(Valcuendeetal2011,Cortes‐Vazquez2012,Cortes‐VazquezandZedalis2013),ithasbeensmalllandownerswhohavemorefiercelyopposedconservationmeasures.Reasonsbehindthis concern the nature of irrigated agriculture in poly‐tunnels, which report substantialrevenueswithout requiring large states.Moreover, this positioning also concern the historicalrelationshipmaintainedwith big landowners. These have been able to capitalise both inmassandnaturetourismatthesametimethatbenefitedfromtherevalorisationoflandsfollowingtheParkestablishment.Inaddition,inrecentyearstheAndalusianGovernmenthasbeenpurchasingprivatelandsinCabodeGataasastrategytoimproveconservationmanagement.ParkManagersacknowledgethatacquiredlandsmostlybelongtobiglandownerswhowereabletoofferlargerplotsatalowerprice.Smalllandownersperceivethiswithdistrust.10MoredetailsaboutthisprocessinCapel(1980).
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in198711.Someofthesescientistssettleddownintheareaandstartedtowork
intheParkOfficeandotherregionalandmixedenvironmentalagencies.Someof
those that remained at their home universities and research institutions also
keptcloselinkswiththisplacebybecomingauthoritativemembersofthePark
GoverningBoard12.
Two particular aspects of expert influence on this area appeal tomy analysis.
Firstly, their findingsnotonlysupportedtheestablishmentof theNaturalPark
but have also informed conservationmanagement up to this time. The values
they have identified, which include endemic plants, communities of migrant
birdsandexceptionalmarineecosystems,arekeyargumentstodefiningwhich
partsoftheParkdeservestricterprotection.Furthermore,theyarealsoessential
to deciding which human‐related elements must be preserved. These include
some archaeological and ethnologic items because of their architectural
singularity(18thcenturycoastaltowers,constructionslinkedtooldminingand
farmingactivitiessuchas farmhouses,watercisterns, terraces,wellsandmills)
or because of their historical contribution to the maintenance of present
ecologicalconditions(forexample,thelinksbetweendryfarmingandrarebirds’
nestinghabits)13.
Secondly, someof these scientists and experts, in their role of ParkManagers,
officers, rangers and guides, have become responsible for meeting the Park’s
conservation goals. As such, their views about the ‘proper’ place of humans in
nature–basedon theWesternmodernnature/societydualism‐permeate their
11TheParkextensionincreasedonceagainin1994.12TheParkGoverningBoard(JuntaRectora,inSpanish)isanadvisoryconsultantpanelformedof different groups of stakeholders (scientists, NGOs, farmers, fisherfolk, local and regionalgovernmentandtourismentrepreneurs,amongothers).Theyperiodicallymeettodiscussissuesconcerning theParkmanagement.However,despite itsname, theironly function is toprovideadvice, lacking any management capability or power to change the Park policy. These areexclusivelyon thehandsofParkOfficersand thedifferentenvironmentalbureaucraciesof theAndalusiaRegionalGovernment.13What isparticularly interestingof thesehuman‐relatedcomponents is that theyaredeemedtheremainingsignsofthe‘traditional’ inhabitantsofCabodeGata,whoareconsideredtohaveheld a ‘wise’ know‐how that permitted them to adapt to a dry environment in an efficient,environmentally friendly way. This form of regarding local inhabitants has acquired greatimportanceintheParkpolicyincurrentyears.Behindit,thereisaseriousattempttointegratehuman presence within the conservation landscape (see similar cases in Anderson andBerglund’s2003editedvolume).Yet,asIwilldiscussinforthcomingsectionsandtheseauthorshavealsostressed,thedepictionof‘traditional’humansandtheirrole,inastylethatrecallsthekindofahistoricalnarrativesanalysedbyWolf(1982),raisesfurtherproblems.
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decisionsandstronglyinfluencethewaytheParkismanaged.Thenextquoteis
agoodexample:
‘TheroleofParkManagersistodecidewhichconservationinitiativesmust
be implemented. For example, if there is an interest in restoring a
watercourse,we need to take into account itsmultiple functions. As key
components of traditional mechanisms for the collection of rainwater,
watercoursesprovideanessentialservicefortheirrigationoforchardsand
domesticwatersupply.Assuch,theymustbekeptfreeofweedandshrubs.
This makes sense, right? But if we study a particular watercourse and
discover that it has now become a preying area for Bonelli’s eagles, for
example,ourdecisionwill thenconsider thisnewecological functionand
prioritise it,because it ismore important than thatofa traditionalwater
supplier’(Male,biologist,memberoftheParkmanagementteam)14
Expertsandexpertcriteriahavealsobeeninstrumentaltothedevelopmentofa
‘green’ tourism industry inCabodeGata.Thismirrors aworldwide trend that
regards tourism as the key to overcome the contradictions between nature
conservation and economic development. New modalities of tourism
(ecotourism, sustainable tourism,nature tourism)have caught theattentionof
institutions andpolicymakers all around theWorld (Ceballos‐Lascuráin 1996,
WestandCarrier2004).InCabodeGata,expertshaveembracedecotourismas
thebesteconomicalternativeforlocalinhabitantsbecauseitsupposedlypermits
themtoliveinthisNaturalParkbymeansofa‘low‐impacting’humanactivity15.
In recent years, ‘visiting a natural place’ has become a powerful gimmick that
attractsthousandsoftouriststoCabodeGata.Thishasrequiredtheintervention
ofParkofficers,whohavedevelopedseveralinitiativestoguaranteethat‘nature’
14Tofacilitatereading,thisandtheotherofquotationsinthispaperhavebeentranslatedfromSpanishintoEnglish.15 The literature specialising in tourism and Protected Areas has questioned this supposedlyflawlessrelationshipandhavestressedtheinfluenceexertedbytouristexpectations‐basedonaWestern rhetoric of wilderness, authenticity or primitive life (Vivanco 2001, Wels 2004)‐ onconservationmanagementbecausetheyurgeParkManagerstotakeactionssothattheseareasbecomeattractive topotential consumers (West andCarrier2004). Inotherwords, to achievethiswin‐winpartnershipbetween conservation anddevelopment through tourismParksmustremainattractiveandaccessiblefortourists,whicheventuallymakeconservationtobesomehowdependantonthesuccessoftourisminitiatives.
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is attractive and accessible for visual consumption. For example, one of the
Park’sattractionsisthatitprovidestouristswiththepossibilityof‘beingcloser
tonature’throughquietcountrysidewalksfarfromnoisy,crowdedandpolluted
urbanenvironments.Tomakethispossible,ParkManagershaveworkedtoward
the design and construction of a network of pathways,with access to vantage
points,signsandanefficientrubbishcollectionsystem.Furtherexamplesinclude
the construction of costly infrastructure (Visitors Centre, Information Points,
Campsites,BotanicGardens)andtheeditionofinformationmaterial(Maps,Park
Guidebooks).Thenextquoteshowsthe importanceParkManagersgive to this
role:
‘In relation to tourism, we do several things: environmental reports,
projects related topublicuseandconservation.Weshouldn’t talkstrictly
about tourism, but about infrastructure, projects and dissemination
materialthatenhancetheParkpublicuse.[…]Forexample,westartedby
building up a Visitors Centre that, like in other Parks, provides a broad
overview of this space. Then we established a few Information Points
alongside the coast, which are open during the high season. We also
workedtowardthecreationofanetworkofpathwaysthatspanalongthe
Park and covers itsmost salient particularities: inland pathways, coastal
pathways and other theme pathways that focus on geological values,
ethnographicorculturalaspects…[…]Alltheseareelementsthatfacilitate
theParktouristicuseandthatdifferentiatethisplacefromanyotherthatis
not a Natural Park’ (Female, biologist, member of the Parkmanagement
team).
The importance of ecotourism gives those that engage with this economic
activityaprotagonistrole inconservationefforts.Ononehand,ParkManagers
havegoodreasonstoaddressecotourismentrepreneurs’requestsbecausethey
have become conservation’s best allies at local level. On the other hand, these
entrepreneurs, a vast majority new ex‐urban inhabitants16, have also good
16 Some other local inhabitants (old farmers and fisherfolk and their descendents) have alsoinitiated some tourism activities, although in a significantly lower proportion. This is clearlymanifested in the marginal position they occupy in the main association of ecotourismentrepreneursthatexistinthePark(ASEMPARNA).
15
reasons to give their support to the Park’s policy for nature protection is
essentialtopreservingtheirownlivelihood.Assuch,ecotourismhasprompted
theemergenceanewsenseofownershipandbelonging,which,asIamaboutto
explain,hasdevelopedduringthelastfewdecades.
The number of new ex‐urban inhabitants in Cabo de Gata has steadily grown
since the first few started to arrive in the late 1960s and 1970s. Fleeing from
urban areas in Spain and other parts of Europe ‐ France, UK, Denmark,
Switzerland,Germany‐ theywere in the look for ‘natural’ locations ‘untouched’
byurbandevelopmentandmodernity,where they sought to commenceanew
‘alternative’ lifestyle. Although they first came as tourists, some of this people
endedupsettlingdown in thearea,purchasingor rentingold farmhousesat a
relativelylowprice17.Asalreadymentioned,theylobbiedwithscientistsforthe
establishmentoftheNaturalPark.Buttheyalsoplayedanimportantpartinthe
development of ecotourism and, through this, in the definition of the Park’s
conservationpolicyandthetransformationofthisarea.
Thedevelopmentofthefirstfewecotourisminitiatives,mostlyaccommodation
andoutdooractivities,waskeyforthesenewgroupstosettledowninthearea.
These initiatives hinged on the utilisation of new images and narratives that
portrayedthisperipheralregionasaplacethatremainedtraditional,naturaland
untouchedbymodernisation; imagesandnarrativesthaturgedtourists tovisit
the area while it stayed authentic and unspoiled18. The establishment of the
Natural Park soon became essential to maintaining these activities since the
quick development of intensive agriculture, mass tourism and industry were
threateningthearea’smainattractions.Infact,itwasbyvirtueoftheParkpolicy
that thisplacebecamean ‘islandofuntouchednature’ anda ‘naturalparadise’
surroundedbyplasticpoly‐tunnels,factoriesandseasideresorts;aphenomenon
thatparadoxicallyincreasedthearea’sappealandattractedmorenewex‐urban
17Housingpriceshadplummeteddue to thedeepeconomiccrisis inpreviousdecadesand thehighlevelsofemigrationthatwerebeingexperiencedatthattime.Furtherparticularitiessuchasexchange rates between national currencies (Deutsche marks or British pounds being muchstrongerthanSpanishpesetas)alsoexplainthis.18Itisinterestingtonotethereferencestoamodernist,linealsenseoftimeintheseimagesandnarratives.Foranexplanationoftherelationshipbetweendualistideasofnature‐societyandthissenseoftimeseeLatour(1993).
16
inhabitants. The next quotation is an example of how thiswas experienced in
firstperson:
‘We opened this hotel in 1988. There were very few people working on
tourismhereby then. Ihadstudied inGermanyandwhenIwasabout to
finishmydegreeandwritemydissertation,Icameheretospendawhole
winter. Itwas the first time I saw this abandoned farmhouse [the actual
hotel]. After asking some people, I finally got hold of the owner andwe
endedupbuyingit.Thefirstthingwedid,asIhadstudiedlanguages,was
offeringSpanishcoursesforforeigners.ThenwestartedTaiChiandYoga
courses.Wegotintouchsoonwithatravelagencywhowereinterestedin
promotingthiskindofinitiatives.Theyincludedusintheircatalogue.You
know,therearelotsofpeopleinGermanythatlookfor‘different’placesto
go on holidays, places outsidemass tourism circuits… people that travel
during low season. Those are the kind of people that come tomy hotel.
Theyareusuallymiddleclassteachers,doctors…whoarelookingforquiet,
original, authentic places. The kind of places you find in Natural Parks.’
(Male,naturetourismentrepreneur,originallyfromGermany)
Throughthedisseminationof these imagesandnarrativesaboutCabodeGata,
thesenewex‐urban inhabitants have also conditioned theway local resources
are managed. The rhetoric that they use in printed vouchers, advertisements,
postcards, websites, blogs and oral communications has contributed to the
definitionofwhat is ‘proper’and ‘improper’ in thisNaturalPark.Assuch, they
place uninhabited valleys and endemic plant species in opposition to cities,
plasticpoly‐tunnelsandirrigatedcrops;ageingmills,oldfarmhousesandsmall
hotels versus factories and tourism resorts. Furthermore, this rhetoric also
differentiates between ‘proper’ and ‘improper’ Park users and inhabitants,
featuring traditional peasants, ecotourists and scientists in sharp contrast to
mass tourism, poly‐tunnel farmers and urban developers. Take Figure 1 as an
example.
Aswewill see in the last section of this paper, the analysis of the Park policy
permitsustoidentifytheextentconservationmeasuresembodythesepeople’s
17
interestsanddesires.However,acloserexaminationofthedifferentdiscourses
that conservation stakeholders enact in relation to conflicts with other local
groups (farmers, fishermen, shepherds, landowners, urban developers) will
furnish us with further evidence of the extent conservation supporters
collaboratetowardsmeetingcommongoalsandtheideasofnaturetheyuseto
doso.Wefocusonthisissueinthenextsection.
PeopleParkConflictsandDifferentIdeasofNature
TheestablishmentoftheCabodeGata‐NíjarNaturalParktriggereddecade‐long
conflictswith some local groups. For example, in the late 1990s social tension
escalated when many farmers and landowners tried to install plastic poly‐
tunnels. They had witnessed the successful development of this activity in
neighbouring areas and were determined to capitalise on it. But, to their
surprise, theydiscoveredthat thiswas forbiddensince1987.Theyarguedthat
the Natural Park had been established without a proper and broad popular
consultation and that this had made many landowners oblivious to the new
regulations.Theyreactedwithangerandcreatedapressuregroup(theARROPE
association)tooverturntheParkpolicy.Evenworse,intheheatofthemoment
somedecidedtodisregardthebansandbuiltuppoly‐tunnelsontheirownlands.
Conservation stakeholders witnessed these issues with horror and decided to
take action. An environmentalist NGO19 and an ecotourism association20
emerged in this context to join forces. They organised meetings and
demonstrations, denounced illegal practices ‐such as new poly‐tunnels‐ on
websites and newspapers21 and urged Park Managers and governmental
agencies to take exemplary actions against offenders. They decried that the
growingpresenceofintenseirrigatedagricultureintheParkwasathreattoits
19AmigosdelParqueNaturalCabodeGataNijar(FriendsoftheCabodeGata‐NijarNaturalPark):http://www.cabodegata.net/20 Natural Park Tourism Entrepreneurs Association (ASEMPARNA in Spanish initials):http://www.cabodegata‐nijar.es/21Seeforexample:‘EcologistasenAccióndenunciaenelTSJAinvernaderosilegalesenCabodeGata’,ElPaís,4/2/1999;‘EcologistasdenuncianblanqueodedineroconinvernaderosilegalesenCabodeGata’,ElPaís,28/3/1999.
18
natural values and accused local farmers and landowners of putting personal
gain before public assets. They lamented that these groups had forgotten the
supposed‘know‐how’thatallowedtheirancestorstomakealivingoffthisplace
withoutharmingtheenvironment.Takethefollowingquoteasanexample:
“Those thathada smallplot,where theyused togrowwheatandbarley,
nowwanttoinstallpoly‐tunnels.Youcan’tevenbreedapairofgoatswith
theyieldsyougetfromdryfarming,butyoucanmakeafortuneoutofpoly‐
tunnels.Thatisgoodbusiness.So,whentheygetintroublewiththePark,
theycan’tcomesaying:‘Oh,wearesopoor!’No,wearenotthatstupid…”
(Male,freelanceandNGOmember,originallyfromAlmeriacity)
Likewise, thesupportgivenbysome localgroups to thedevelopmentofmass‐
tourism in the Park has also raised similar conflicts with conservation
stakeholders. Especially controversial have been certain initiatives developed
within or near the border of the Protected Area. Because of its international
notoriety, the Algarrobico Hotel case is perhaps the best example. The
constructionofthishotelontheAlgarrobicobeach,nexttothetownCarboneras,
in the earlier part of the 2000s sparked the outrage of conservation
stakeholders. They vilified it and accused it of trespassing the red line that
separatestheParkfromitssurroundings,whilecriticisingthedamageitwould
causetovaluableecosystems.Theytooktheiractionsevenfurtherthis timeas
they brought the case into court and initiated an international campaign to
denouncethatthishotelwasillegallyconstructedwithinaProtectedArea22.
Finding out legal responsibilitieswas to become a drawn‐out judicial process.
Meanwhile multiple demonstrations organised by both hotel supporters and
hoteldetractorsrevealedwideningsocialdivisionswithin thePark.Some local
groupsdefendedthatthehotelwasessential tocreatingmuch‐needed jobs.On
the contrary, conservation supporters alleged that localpeoplewereunable to
22 Different news items appeared in several international newspapers are evidences of this:«Building blight on Spanish coastline», The Guardian (7/7/2006); «Costas turn back tide byblowingupanewhotel»,TheTimes (12/6/2006); «Espagne:Greenpeace recouvred’une toilegéante une construction illégale» Le Monde (12/2/2009); «Naturpark in Spanien: GreenpeaceverhulltillegalgebautesHotel»,DerSpiegel(12/2/2009).
19
appreciatethenaturalvalueandbeautyofthisarea,itsexceptionalfeaturesand
thenecessitytoavoiditsdestruction.
Theanalysisoftheseconflicts,aswellasmanyoftheothersthathaveemerged
in relation, for example, to land ploughing, in‐shore fishing, grazing and fish
farms23,revealsunderlyingaspectsofconservationstakeholders’argumentsthat
gobeyondthevalueofnaturalassetsandthatrelatetonewsensesofownership
and belonging. As such, it is frequent to encounter the opinion among these
stakeholders that nature conservation is also a way of preserving people’s
livelihood.Forthem,theconstructionofnewhotelsandpoly‐tunnels,aswellas
thegrazingofendemicspeciesorfishinginmarinereserves,threatenthevalues
onwhich ecotourism relies.They reprimand those in favourof these activities
for damaging nature and impairing the successful development of a green
tourismindustry.Inotherwords,theyreproachthelocalsforgoingagainsttheir
meansofliving,whichdependontheprotectionofnaturefromcertainformsof
humanexploitation.Thefollowingquotesillustratethis:
‘Theydon’t care that this is apublic asset... Theydon’t care that this is a
Natural Protected Area… With the Algarrobico Hotel, the illegal poly‐
tunnels, urbandevelopments… theyare just looking to fiddle the system!
There iswhere you realise howweak this is…This is aNature Park and
herebothnatureandhumansareprotected:thosewholiveinsidethePark
andwhosemain activities depend on the Park being just theway it is…
WiththeAlgarrobicoHotel,whatkindofshamelesspersonwouldsellthis
hotelonthebasisthatit’sinaNaturalPark?ThisisthemostAnti‐Natural
Park thing I’ve ever seen!’ (Female, ecotourism entrepreneur, originally
fromMadrid)
‘This [place]hasabigproblemwithovercrowding.Andall thesenewbig
hotels are only bringing more and more tourists. This place has very
sensitive areas where even walking might cause a great impact on rare
plantandanimalspecies,becausetheycanbesoeasilydamaged.Youcan23Seeforexample:«EcologistasenAcciónprotestacontralacreacióndeuncriaderodelubinasenCabodeGata‐Níjar»,ElPaís (14/3/1999); further examples canbe found in theAmigosdelParque NGO’s self‐edited journal El Eco del Parque: «Roturaciones ilegales en La Isleta y LosEscullos»(32/2004);«RoturaciónenSanMiguel»(40/2006).
20
killalltheseendemicspeciesifyouarenotcarefulenough.Andifweruin
this,weruinournaturalheritageandourmainsourceofincome.Theysay
we [ecotourism entrepreneurs] are environmentalists, like in a negative
way…But,apartfromoureducationandideology,Ialwaysanswer:Those
of us who live off this Park are its main defenders, because it not only
concerns our ideals but also our way of subsistence, our life!’ (Male,
ecotourismentrepreneur,originallyfromAlmeriacity)
Likewise, scientists and experts also acknowledge this problemandagree that
conservationmeasures are justified not only because they preserve the Park’s
natural values but also because they preserve the livelihood of the Park
inhabitants.Takethefollowingquoteasanexample:
‘Tourismplaysavery importantrole inthePark,especiallybecausemost
other activities [farming, fishing] are currently a minority. The main
incomefortheParkinhabitants istourism,butthis isthreatenedbecause
most touristsonlycome inhighseasonandalsobecause theyallwant to
havetheirownsummerhouseintheParkandthatdamagesnature.Thatis
incompatible.’(Female,biologist,memberoftheParkmanagementteam)
Despite some punctual internal disagreements between Park Managers,
ecotourismentrepreneurs,NGOmembersandscientists24,theprotectionofCabo
de Gata has always remained a common and shared goal. As we have seen
throughout this and the previous section, different and multiple situated
interests and desires are behind the support given to the Park policy. What
remainstobeexaminedishowtheParkpolicyhasaddressedtheseinterestsand
desiresandhowmodern ideasofnaturehavebeenused inorderto justify the
transition inmanagement roles thatmadepossible the transformationofCabo
de Gata from a farming and fishing area to an ecotourism destination and
biodiversityreserve.
24Furtherclarificationisrequiredatthispoint.AlthoughforthesakeofclarityandbrevityIhavemade an effort to present the position of all these different conservation stakeholders assomehowhomogeneous,therealsituationisnotsoneat.Overthelasttwodecades,therehavebeen several conflicts between them, in particular as NGO members and ecotourismentrepreneursurgedParkManagerstotakemoresevereactionstostoptheinstallationofpoly‐tunnels,illegalploughings,fishfarmingandtheconstructionofnewhotels.
21
ConservationMeasuresandtheNaturalizationofCabodeGata
Themost importantmanagement tool in the Park is the land‐use zoning plan.
Thefirstplancameintoforcein1994anddividedthePark’stotalextensioninto
four zones (A,B,C,D) and ten subzones,boundingeachof them toadifferent
degree of protection.Whilstmost activitieswere forbidden in Zones A and B,
manywereallowedinZonesCandD.Thiszoningplanwasinforceforfourteen
years, until a new one was approved in 2008 without major differences. I
summarisethe2008planinTable125.
What isparticularlyrelevant tomydiscussion ishowthePark land‐usezoning
plansmakeuseofcertainenvironmentalnarrativesbasedonthenature‐society
dualism inorder to justifydifferent levelsof restriction.Forexample,ZonesA,
where the most restrictive measures apply, are deemed virgin natural areas
barelytransformedbyhumanaction.Onlyconservationpracticesandscientific
research are allowed in them. In Zones B the Park policy allows some non‐
intensive farming, fishingandgrazingpracticesaswell asecotourism.ZonesB
areregardedassemi‐naturalareas,where‘traditional’practiceshaveshapedthe
local ecosystems in such a non‐aggressive way that there are still significant
values in them. In Zones C and D most practices are allowed, even intensive
agriculture,althoughunderthesupervisionofParkManagers inordertoavoid
any harm to those natural values found in other parts of the Park. Thismore
permissive regulation is justified because Zones C and D are said to lack
significantnaturalvalueduetoyearsofhumanexploitation.
Thisdivisionintocompletelynatural,partiallynaturalandbarelynaturalareas
showstheinstrumentaluseofdualisticideasofnature‐societyinthejustification
of land‐use changes. Themodern,Western ontological premises that underpin
theseideas,asdiscussedbyLatour(1993),explainthatthemoretransformedby
humansanarea is judged, the lessnatural it is considered,which involves less
restrictivemeasures.However, a closer look into thekindofactivities thatare25 The original documents can be acceded at the environmental section of the AndalusianGovernmentwebsite:http://www.juntadeandalucia.es/medioambiente/site/portalweb/Lastacceded:June2011.
22
eitherallowedorforbiddenineachzoneunfoldsaparadox:thecounterintuitive
utilisationofmodernist ideasofnature, inasmuchastheland‐usezoningplan
renders certain activities either essential or compatible with nature
conservation.As Iwillexplain in theremainingparagraphsof thissection, this
suggeststhattheseideasofnatureareutilisedtograntcertaingroupstheright
tousenaturalresourcesaswellastodisenfranchiseothers,insteadoftoprotect
theParkfromhumanintervention.
AnanalysisofthemechanismthatmakestheabovepossibleshowsthatthePark
land‐usezoningplannotonlyconveysaredefinitionofthephysicalenvironment
but also of social relations. This redefinition of social relations is articulated
around a new social hierarchy, which hinges on a new categorisation and
classification of human‐environment relations into: 1) modern and intense
activities, suchasagriculture inplasticpoly‐tunnels,mass tourism,miningand
industry, which are regarded as potential destroyers of the Park’s assets; 2)
customary, non‐intensive farming, grazing and fishing practices, which are
considered somehow respectful to the environment because they have
historically produced valuable semi‐natural ecosystems by making use of an
ecologically wise know‐how; 3) modern, environmentally friendly activities,
such as ecotourism, that make conservation and economic development
compatible because they exclusively rely on the visual consumption of nature;
and 4) scientific research, environmental education and conservation
management, which are considered essential to the correct preservation of
nature. For the sakeof clarity, I simplify this in fourdifferent roles, defined in
terms of the relationship they are said to maintain with nature: 1) nature
destroyers,2)natureproducers,3)natureconsumersand4)natureprotectors,
respectively.
Table2summarisesthecompatibilitiesandconflictsassociatedtotheserolesin
the different parts of the Park, according to the land‐use plans. The table also
permits us to visualise the new social hierarchy that regulates land‐use rights
and distribute uneven access to natural resources among the different local
groups. As such, it becomes the most important mechanism to meeting
conservation goals, including not only the supra‐local concerns that aim to
23
protectEuropeanperipheralregionslikeCabodeGatawhilepromotingaservice
economy, but also the situated interests and desires of local conservation
supporters.
Scientists and experts are on top of this hierarchy. Their research and
administrationactivityareallowedallalongtheProtectedArea,eveninZonesA,
whichshouldsupposedlybekept free fromhumanaction.Astepbelowin this
hierarchywefind‘traditional’farmersandfishermenaswellasecotouristsand
ecotourismentrepreneurs.Thepeoplebelongingtothesegroupsareallowedto
carryouttheirpracticeswithinsomepartsofthePark(ZonesB,CandD)butnot
in Zones A. However, they are not completely free to decide how to use local
resourcesfortheiractivityisalwayseitherdirectlyorindirectlymonitoredand
controlledbyexpertsandscientists.Finally,atthebottomofthishierarchythere
are those who engage with modern, intensive activities (poly‐tunnels, urban
developmentandindustry).Theiractivitiesarebannedwithinmostpartsofthe
Park,and,intherarecasetheyareallowed–mostlyinthoseareascataloguedas
non‐natural‐,theyneedtoadjusttothemultiplerequirementsimposedbythose
peopleatthetopofthishierarchy,sothattheseactivitiesdonotimpactnatural
orsemi‐naturalareas.
A final critical examination of this hierarchy in relation to the issues analysed
throughout this paper permits us to identify the intimacies between the Park
conservationpolicyandthesituatedinterestsanddesiresofthosestakeholders
that this paper centres on. Although both ‘nature producers’ and ‘nature
consumers’havetherighttouse localresources inmanypartsof thePark, the
analysiscarriedoutinabovesectionssuggeststhattheyhaveadifferentcapacity
toinfluencetheParkpolicy.AsIhopetohavealreadydemonstrated,therelation
betweenexperts,Parkofficers,ecotourismentrepreneursandthenewex‐urban
populationatlargeiscloseenoughtodenythat‘natureconsumers’holdamuch
moreprivilegedpositionthan‘natureproducers’inwhatconcernstheircapacity
toinfluencetheParkpolicy.
Furthermore, the role of ‘nature producers’ compel farmers, shepherds,
fishermenandlandownerseithertobehavethewayconservationsupporterssay
24
that ‘traditional’ inhabitants should behave or to engagewith ecotourism and
become ecotourism entrepreneurs. Otherwise, if they attempt to capitalise on
poly‐tunnels ormass tourism, theywill beputting themselves at riskof facing
prosecutionforcontraveningtheParkplans.Thisshowstheirlackofinfluencein
resource management for the Park plans relegate them to a position that is
actuallyclosertothatof‘naturedestroyers’thanto‘natureconsumers’,because
theybothenduphavinganullcapacitytoinfluencetheParkpolicyandtogive
voicetotheirowninterestsanddesiresintheParkland‐useplans.Assuch,the
‘Naturalization’ of Cabo de Gata has less to do with the limitation of human
impactontheenvironmentandmorewitharedefinitionofland‐userightsthat
grant the control of natural resources to conservation stakeholders, while
disenfranchisingthoseothergroupsthatopposeorquestionconservation.
Conclusions
Ihavetriedtodemonstrateinthispaperthattheutilisationofmodernistideasof
nature is essential to the collective appropriation of Cabo de Gata by certain
social groups because it justifies a new way of managing local resources in
accordancewith their interests and desires. This suggests that conservationist
argumentsdonotmerelyhingeon theunquestioned capacityof scientists and
experts to protect nature from human aggressions neither on the ontological
premises ofWesternnaturalism that has historically been so influential in the
conservationfield.Thesearejustpartoftheconceptualapparatusthatenablesa
transition inmanagementroles, throughwhichnewempoweredgroupswhose
livelihood and desires are rooted in keeping places sparsely populated, barely
urbanisedandvisuallyattractiveforecotourists,aregrantedtherighttocontrol
andusethisterritory,allowingforitstransformationintoabiodiversityreserve
andecotourismdestination.
The ethnographic analysis of people‐park conflicts in the Cabo de Gata‐Níjar
Natural Park provides clear evidence of this phenomenon and permits us to
identify some of its political and economic drivers. Any questioning of the
naturalizationofthisplace,suchasthatsupportedbyfarmersandlandowners,
25
is deemed a threat not only to natural values but also to many stakeholders’
livelihoods because it hinders the successful development of ecotourism. To
ensurethefutureofthisactivity,theParkpolicyrelegatesconservationobjectors
to a powerless role so that their demands and land‐use rights ‐whether
stemmingfromlandownershiporhistoricalbonds‐aresuppressed.Insteadthe
Park policy grants these rights to those who, despite lacking either land
ownershiporhistoricalbonds,havegainedsignificantpowerfromthesupportof
supra‐local institutions (EuropeanUnion), thespurofa fast‐growingeconomic
activity (ecotourism) and the moral justification provided by a globalised
greeningrationale.
Theabovehasdeep implications for thestudyofpeople‐parkconflictsand the
problemsassociatedtothepromotionofmoreenvironmentallyfriendlywaysof
mastering the environment. The establishment of this Natural Park is to be
understood within a context where new actors intervened in a space that
became ‘naturalized’. Animals, plants and ecosystems acquired newmeanings
and values,which justified the introduction of conservationmeasures and the
development of ecotourism as an alternative to activities such as intensive
agricultureandmass tourism.As such, this storymustbe read in termsof the
powerrelationsthataccompaniedaprocessofterritorialappropriation;anditis
in this sameway that we need to frame the disagreements and contestations
articulatedbyotherlocalgroups,suchasfarmers,fishermenandlandowners.
This is especially important if we consider that one of the main critiques
emerging fromtheexaminationof conservationpractices inProtectedAreas is
that they distribute fortune andmisfortune among different social groups and
even different members of a particular group (Brockington et al 2008).
Sometimes this is caused directly, through physical evictions, sometimes
indirectly,throughsymbolicalienation.Thismeansthatmostsocialproblemsin
conservation‐targetedareas–problemsthatarepronetothreatenconservation
goals‐havelesstodowithenvironmentaleducationandmorewiththedifferent
aspectsofatransitioninmanagementrolesovernaturalresources,whichtend
todisregardtheinterestsanddesiresofmanylocalinhabitants.
26
Finally,whatalsoseemsclearfromtheanalysisIcarriedoutinthispaperisthat,
fifteenyearsafterArturoEscobar(1999)foresawtheendofWesternnaturalism,
rather than giving way to less essentialist accounts of the reality ‘out there’,
modernideasofnatureprevailandinsomecaseshaveevenbecomereinforced
forpoliticalandeconomicreasons.Theanalysiscarriedoutinthispaperaddsto
thosesuggestingthatnaturalismisstillapowerfulworldviewthatdictateshow
we should relatewith the environment and thatProtectedAreashavebecome
one of the main material and discursive means to achieving this (West et al.
2006).Italsoshows,asYates‐DoerrandMol(2012)suggest,thatifwewantto
make naturalism the object of ethnographic research, we need to trace the
practicesofthosewhobearthisworldviewandexaminewherethepowerthat
fuelsitsexpansionemanatesfrom.
27
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1
Acknowledgements:
Anearlierversionofthispaperwaspresentedatapanelentitled‘Masteringthe
environment?’ (Knut G Nustad and Signe Howell, organisers) at the 2012
biannualmeetingoftheEuropeanAssociationofSocialAnthropologistsinParis,
France. Iwant to thank theorganisers for their encouragement topublish this
workaswellasAlexandraTowersandMartinaPrendergastfortheirediting.
1
Table1:ZoningCategories
Zonescategories
Subcategories Name Extension(ha)
PercentageofPark
ZonesA1 InlandreserveA ZonesA2 Marinereserve 6479 13,6%
ZonesB1 NaturalAreasofGeneralInterest 19438 39,3%
ZonesB2Semi‐naturalAreaswithTraditional
Uses7129 14,4%
ZonesB3 Leisurecoastalareas 154 0,3%
ZonesB4 UrbanBeach 27 0,1%
B
ZonesB5 Fishingandleisuremarinearea 9614 19,4%
ZonesC1 Areaofagriculturalcrops 2831 5,7%
ZonesC2Areaofintensiveagricultureunder
plastics551 1,1%C
ZonesC3 UrbanArea 269 0,5%
D ZonesDZonesoutofenvironmentalregulation
Rest Rest
1
Table2:SummaryofConservationCompatibilitiesandConflicts
NatureProtectors:Scientificactivities,
environmentaleducation,conservationmanagement.
NatureProducersandConsumers:Traditional,non‐intensiveactivities,ecotourism.
NatureDestroyers:Modern,intensiveactivities
Naturalareas(ZonesAandsomeZonesB) COMPATIBLE CONFLICTIVE CONFLICTIVE
Seminaturalareas(MostZonesB) COMPATIBLE COMPATIBLE CONFLICTIVE
Nonnaturalareas(ZonesC&D) COMPATIBLE COMPATIBLE COMPATIBLE