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ContentslistsavailableatScienceDirect

Land

Use

Policy

jou rn al h om ep a g e :w w w . e l s e v i e r . c o m / l o c a t e / l a n d u s e p o l

Exploring

the

relationship

among

local

conflicts

and

territorial

vulnerability:

The

case

study

of

Lombardy

Region

Alessandra

Oppio

a

,

Stafano

Corsi

b,∗

,

Sergio

Mattia

a

,

Andrea

Tosini

b

aDepartmentofArchitectureandUrbanStudies(DAStU),PolitecnicodiMilano,viaBonardi3,20133Milan,Italy

bDepartmentofEconomics,Management,andQuantitativeMethods(DEMM),UniversityofMilan,viaCeloria2,20133Milan,Italy

a

r

t

i

c

l

e

i

n

f

o

Articlehistory:

Received10January2014

Receivedinrevisedform31October2014 Accepted10November2014 Keywords: Vulnerabilityassessment Localconflicts Overlaymapping Lombardyregion

a

b

s

t

r

a

c

t

Duringthelast10years,oppositionbylocalcommunitiesagainstthedevelopmentofindustrial facili-ties,energytechnologiesandtransportinfrastructureshassteadilygrown.Negativeexternalitiesonthe environment,qualityoflifeandhealtharethemostfrequentmotivationsoftheopponents.Disputes aretypicallygroundedinenvironmental,socialandeconomicconcernsaboutthelocalimpactsofnew developmentproposals.Withinthiscontext,thispaperaimstoexploretheexistenceofapotential rela-tionshipbetweenthelevelofterritorialvulnerabilityandthedistributionoflocalconflictssurveyed bythelocalandnationalpressintheLombardyRegion(Italy).Thistypeofrelationshipisinvestigated usinganempiricalanalysisbasedonanoverlaymappingofdifferentinformativelayers.The vulner-abilityindexhasbeencalculatedaccordingtothemostrecentconceptualandanalyticalframeworks developedinthescientificliterature.Itisamultidimensionalindexgroundedinenvironmental,social andeconomiccriteria.Theoutputsofthevulnerabilityassessmenthavebeenplacedintothematicmaps toprovideacomprehensiveoverviewoftheenvironmentalandsocioeconomicstateoftheLombardy Region.Inadditiontothegeneraldegreeofvulnerability,themapsdisplaythelocalconflictssurveyedby theNIMBYForum,anItaliansurveyofterritorialdisputesmanagedbytheAgencyofResearchand Infor-mationSociety.Themapsprovideameansofi)puttingforwardsomehypothesesabouttheoppositions thathaveemergedaroundthelocalizationofnewfacilities,includingmainlyindustrialfacilities,waste disposals,energyplantsandtransportinfrastructures,andthevulnerabilityoftheLombardyRegion;ii) identifyingthedrivingfactorsofterritorialvulnerability;iii)investigatingwhetherthelocaloppositions aredirectlyproportionaltoterritorialvulnerability.Thefirstresultsindicatethatadirectrelationship amongterritorialvulnerabilityandconflictsdoesnotexist.Thisoutcome,evenonapreliminarybasis, providesanewanalyticalperspectiveforunderstandingthereasonsbehindlocalcommunityprotests.

©2014ElsevierLtd.Allrightsreserved.

Introduction

Thestudyofvariousinteractionsbetweenpeoplethatarethe

resultofconcernsforenvironmentalqualityisafieldofresearch

thathasbeencomprehensivelyinvestigatedsincethesecondhalf

ofthelastcentury;thisistheresultofthegrowingpublic

aware-nessofthenegativeexternalitiesofhumanactiononthenatural

landscape.Asmanyscholarshaveclaimed,noeconomicactivityis

exemptfromexternalities(Pigou,1948;Mishan,1965;Boulding,

1966;BardeandGerelli,1980;Roegen,1971).

Thus, many theoretical perspectives and methodological

approachesforunderstanding,evaluatingandprovidingoptions

∗ Correspondingauthor.Tel.:+393403770163. E-mailaddresses:alessandra.oppio@polimi.it(A.Oppio), stefano.corsi@unimi.it(S.Corsi).

forlandusetoensurethathumanhabitationadheresto

sustaina-bilityprincipleshavebeendeveloped(Ndubisi,2002).Themost

relevantthreattothesegoalsis thelossin theecologicalvalue

ofenvironmentalresourcesandtheresultingdecreaseinhuman

well-being.Environmentalandsocio-economicvulnerabilityistoo

often neglected in decisions regarding territorial and/or urban

redevelopmentinterventions,asindicatedbytheamountoflocal

communityoppositionagainstfacilitiesthatareperceivedasa

dan-ger(MattiaandOppio,2008).Theoppositionoflocalcommunities

tonewinfrastructuresandplants,theso-calledNIMBY(NotInMy

BackYard)syndrome,areconsideredaproxyindicatorofthelevel

oftheperceivedrisk.Manyscholarshaveexaminedthecausesof

localconflictsindifferentfieldssuchasurbanizationinagrarian

landscapes(DarlyandTorre,2013;Torreetal.,2014),the

commit-teeagainstextractiveindustry(Hilson,2002),andtheinterferences

betweenwindpowerandmilitaryaviation(Lindgrenetal.,2013).

Othershaveprovidedsuggestionsforlanduseconflictresolution

http://dx.doi.org/10.1016/j.landusepol.2014.11.006 0264-8377/©2014ElsevierLtd.Allrightsreserved.

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240 A.Oppioetal./LandUsePolicy43(2015)239–247

basedforthemostpartoncommunityinvolvementin

decision-makingprocesses(RauschmayerandWittmer,2006;Wittmeretal.,

2006;Nijniketal.,2009;Hesseletal.,2009;Kamruzzamanand Baker,2013;MagsiandTorre,2013;Saarikoskiaetal.,2013).

Thepotentialnegativeimpactofinfrastructureandplantsonthe

environmental,economicandsocialsystemsshouldbeconsidered

afurtherpressurefactor(BradleyandSmith,2004),especiallyfor

thoseterritoriesthatarehighlyvulnerableasaconsequenceoftheir

susceptibilitytoharmorhazard(Menonietal.,2011)ortotheir

inabilitytocopewithexternalevents(Cutteretal.,2003;Turner

etal.,2003;Berryetal.,2006;Metzgeretal.,2006;Smithetal., 2008).

Changesinlanduse,socio-economiccharacteristics,

biodiver-sity,atmosphericcompositionandclimatereducethecapability

ofaterritorythatismeanttobeanecosystemthatprovidesvital

servicesforpeopleand societysuchasbiodiversity, food,fibre,

waterresources,carbonsequestrationandrecreation(Costanzaet

al.,1997;DeGrootetal.,2002).

Within this context, the concept of vulnerability has been

increasinglyconsidered,asit revealsthedegreetowhicha

ter-ritorialsystemislikelytoexperienceharmduetodifferenttypes

ofthreats,andthegoalhasbeentoprovidereliableinformationfor

policyanddecisionmaking(GolobiˇcandBreskvar ˇZaucery,2010).

Furthermore,vulnerabilityisthesusceptibilityofagiven

popula-tion,system,orplacetoharmfromexposuretothehazard,andit

directlyaffectstheabilitytopreparefor,respondto,andrecover

fromhazardsanddisasters(Cutteretal.,2009).Ontheonehand,

itfocusesonthestateofaterritorydescribedbyaspecificsetof

criteria.Ontheotherhand,italsoreferstohowthenaturaland

humanenvironmentcanrespondtoexternalevents(Toroetal.,

2011)thathavethepotentialtobecomeworse(BradleyandSmith,

2004).Accordingtotheecosystemapproach(MilleniumEcosystem

Assessment,2005),vulnerabilityisamultidimensionalnotion,as

itregardsnotonlytheenvironmentalandphysicalissuesbutalso

thesystemic,social/community/institutionalandeconomicones

andtheirrelationship(Cutteretal.,2003;Menonietal.,2012).

Thevulnerabilityoftheterritorywithrespecttotherealization

ofinfrastructurescanalsobeassociatedwithlandconsumption

andtheimpactontheagriculturalsystem(Mazzocchietal.,2013;

Torreetal.,2014).Becausethisnotionhasbeenstudiedin

sev-eralfields,manycomplementarydefinitionshavebeendeveloped

accordingtodifferentconceptualmodelsandframeworkswith

dif-ferentmethodsofmeasurement(Tranetal.,2010).

Althoughthemanydefinitions ofthenotionof vulnerability

highlightthedifferentfacesofthesameconcept,theyallfocuson

thefollowingconcepts:i)vulnerabilityisanintrinsicfeatureofa

systemthatcanbedescribedbytheuseofaspecificsetofcriteria;

ii)thenotionofvulnerabilityismultidimensionalasitaffectsnot

onlytheenvironmentalaspectofaterritorybutalsotheeconomic

andsocialonesandtheirmutualrelationships.

Thedefinitions ofriskareseveral.Thedefinitionusedinthe

LegislativeDecreeno.81of2008,whichfollowstheoneproposed

byCutter (Cutteret al., 2000), defines “risk” asthe product of

thelevelofdamage intheconditionsofuseand thefrequency

ofadverseevents(D.LgsNo.81of2008,Article2).Thedefinition

conformstothefollowingformula:

R=D∗F

whereRrepresentstherisk,DfordamageandFforthefrequency

ofharmfulevents;theterritorialvulnerabilitycouldaffectboththe

frequencyandthelevelofharm.Thedevelopmentofinfrastructure

inavulnerablecontextstrengthenstherisk,asitincreasesthe

fre-quencyandthesignificanceoftheharmfulevents.Thus,therisk(R)

shouldbecommensuratetothedegreeofterritorialvulnerability

(V): R∼V

Atthesametime,theconflicts(C)shouldbeproportionaltothe

risk,asthelocalcommunitiesgenerallyhinderthedevelopmentof

interventionsperceivedasdangerous:

C∼R

Consequently,thelevelofdisputesagainstfacilitiesshouldbe

balancedwiththedegreeofterritorialvulnerability:

C∼V

Starting fromthis conceptual framework, thepaper aimsto

exploretheexistenceofapotentialrelationshipbetweenthelevel

ofterritorialvulnerabilityandthedistributionofthelocal

commu-nityoppositiontothedevelopmentofindustrialfacilities,energy

technologiesand transport infrastructures.Data about protests,

surveyedbytheItalianPermanentMediaObservatoryofNimby

Forum,indicatethatterritorialdisputeseffectivelyariseinthemost

industrializedandurbanizedregions.

Thegeographicaldistributionoflocaloppositionhasbeen

deter-minedbyanempiricalanalysisbasedontheoverlaymappingof

differentinformativelayers.

Thevulnerabilityassessmentcombinedwiththespatialanalysis

ofdisputeshighlightsthecriticismofthecomplexdecision-making

processesandsuggestsrelevantinsightsforbetterunderstanding

thereasonsfor localopposition.For instance,the identification

ofthecostsand benefitsofnewfacilitiesdependsontheirsize

andscope.Consequently,thenumberofstakeholdersinvolvedis

generallyaffectedbytheterritorialleveladoptedforvulnerability

assessment.

Thispaperisdividedintothreeparts.Thefirstpartfocusesonthe

methodologyformeasuringtheterritorialvulnerability.The

sec-ondpartdisplaystheterritorialvulnerabilityprofileofLombardy

provinceswithradarchartsandvulnerabilitymaps.Thethirdpart

isdedicatedtotheanalysisoftheemerging issuesbya

territo-rialvulnerabilityassessmentcombinedwithaspatialanalysisof

localconflicts.Theoverlaymappingofthevulnerabilityindexand

thelocalizationofoppositions,althoughempirical,representsan

interestinginvestigationaboutthereasonsforthedisputes.

Materialsandmethods

ThedefinitionoftheVulnerabilityIndex

TheVulnerabilityIndex(VI)hasbeencalculatedaccordingtothe

methoddevelopedbyToroetal.(2011)becauseitconsidersboth

theenvironmentalandsocio-economicvariables.

TheVIisgivenbythesumofthevulnerabilityvalueofeachof

thefollowingcriteria:

VI=IWD+IFD+ILUC+ISWQ+IAQ+ISS+IPp+IEp+IEdu

whereIWHisthevulnerabilityvalueofwildlifehabitat;IWHofthe

floradiversity;ILUCofthelandusechange;ISWQofthesurfacewater

quality;IAQoftheairquality;IEpoftheemployment;IPpofthe

pop-ulation;IEduoftheeducationalsystem;IWHofthesocialsecurity.

Thevulnerabilityvalueatthelevelofcriteriaisnormalizedonthe

basisoftheminimumandthemaximumvalueofeachvariable

accordingtothefollowingformula:

Ni=(Xi−Xmin)/(Xmax−Xmin)

whereNiisthenormalizeddata,Xiisthedatatobenormalized,

XministheminimumvalueassumedbythevariablesandXmaxisthe

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Fig.1.Lombardyregion;Landuse,Provinces,Neighbouringterritories.

thecurrentstepoftheresearch,thevaluesoftheindexreflectthe

levelofvulnerabilityofeachfactorwithreferencetoaneutral

sce-nario.Itshouldberelevanttointroduceaweightingsystemforthe

criteriaonthebasisofboththetechnicalanalysisofthestrengths

andweaknessesofaspecificterritoryandtheinvolvementoflocal

communities.

TheanalysishasfocusedonLombardy,asitisoneoftheItalian

regionswiththehighestamountoflocalcommunityopposition

in thelast tenyears as measuredby theNimby Forum annual

survey.Giventhesubdivisionofthecountryintothree

adminis-trativelevels(Regions,ProvincesandMunicipalities),theVIhas

beenperformedattheprovincelevelbecausethemajorityofthe

conflictsrefertolinear(e.g.,roadinfrastructureandhigh-voltage

lines)orpunctual(e.g.,airportinfrastructure,industrialplants,and

biogasplants)developmentproposalsthathaveanimpactonthe

sub-regionalterritorialscale,forexample,theprovinces.

Casestudy:theLombardyregion

TheLombardyregionhasasurfaceof23,858km2anda

pop-ulationof9,400,000inhabitants (RDP,2007).Nearly50%ofthe

regionalterritoryislowlying,morethan40%ismountainous,and

therestishilly(Fig.1).Ruralareascover82%oftheterritoryand

areinhabitedby35%ofthepopulation.Regionalpopulation

den-sityis408inhabitants/km2,muchgreaterthanthenationalaverage

(199ab/km2)(Corsi,2009).Thedemographicalstructureisaffected

byadecliningbirthrateandanincreasinglifeexpectancy,and53%

oftheregionaladultpopulationhasacompleteeducation

(upper-secondaryandsuperior).Thispercentageincreasesto73%amongst

youngpeople.TheLombardyregiongeneratesmorethan20%ofthe

ItalianGDP.TheeconomicstructureofLombardyischaracterized

bytheimportanceofthesecondaryandtertiarysector.In2003,

theGDPpercapitawas28,254euro(40%morethanthenational

average).

Nearly57%oftheregionalterritoryisdedicatedtotheprimary

sector,whilethetotalUAAcovers43%ofit.

Aportionof15%oftheregionalterritoryfallsunderNatura2000,

withatotalsurfaceofapproximately370,000Haand245sites,and

thereare92parksandotherprotectedareasthatcover131,000Ha

(Fig.2).Urbanand peri-urbanareashavea greatimportancein

termsof population(morethan5.9millionpeople) andsurface

andhaveadensityofnearly1400inhabitants/km2.TheLombardy

regionholds,togetherwiththeVenetoregion,theprimacyofthe

urbanizedlandthataffects13%ofthetotalarea(ISTAT,2013).The

urbanareaismadeupofthemaintowns(Bergamo,Brescia,Monza

andBrianza)andthelargeconurbationofMilan.TheLombardy

regioniscrossedbyoneofthelargestnetworksofinfrastructure

inItaly:Therailnetworkisextensive,with80.6kmper1000km2

(Corsi,2009);theroadnetworkisjustunder12,000kmand

rep-resents 7.9% of the national road network (Annuario Statistico

Regionale,2011).Intheregion,therearealso14airports,ofwhich

5areforcivilianuse(AnnuarioStatisticoRegionale,2007).Inthe

Lombardyregion,7landfills(ISPRA,2012)and13waste-to-energy

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242 A.Oppioetal./LandUsePolicy43(2015)239–247

Fig.2.Lombardyregion:Protectedareas,Parks,Reserves. Source:AreeprotettedellaRegioneLombardia(2013).

plants,37.6%arepresentinLombardy(CRPA,2013).TheSIRENA

projectintheLombardyregionhasidentifiedapproximately24,000

powerplants rangingfromhydroelectric plants tophotovoltaic

power(the mostnumerous) to plant biomass in power plants

(FINLOMBARDIA,2012).In2012,theAuthorityforElectricityand

GasmeasuredintheLombardyregion127,348kmof electricity

distributionnetworks,morethanallotherregions(Autoritàper

l’energiaelettricaeilgas,2012).

TheVulnerabilityIndex(VI)hasbeenstructuredthroughthe

measurementofenvironmentalandsocioeconomiccriteria,

quan-tified byspecific criteria as suggestedby the above-mentioned

researchbyToro(seeTable1).

Table1

Vulnerabilitycriteria.

Criteria Acronym Indicators Sources Year

WildlifeDiversity WD Numberofthreatenedspecies CentroFloraAutoctona

(LombardyRegion)

2008

FloraDiversity FD Numberofthreatenedspecies CentroFloraAutoctona

(LombardyRegion)

2008

AirQuality AQ AirQualityIndex ARPALombardia:Regional

agencyforenvironmental protection

2011

Landuse LUC Percentageofnaturalareas DUSAF2.1(DestinationofUse

ofAgriculturalandForestSoils) LombardyRegion

2010

SurfaceWaterQuality SWQ Sewagetreatmentchannelled

intothedrainagesystem

ATO(AmbitoTerritoriale Ottimale)LombardyRegion

2007

SocialSecurity SS QualityofLifeIndex ILSOLE24ORE(annualsurvey) 2012

Population Pp Populationdensity ISTAT(populationsurvey) 2013

Employment Ep Unemploymentrate ISTAT(labourforcesurvey) 2012

Educationsystem Edu Averageyearsofeducationof thepopulationover15years

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Fig.3.TheVulnerabilitymapofeachprovince.

Ashortsummaryofthecriteriaisprovidedafterward.

RegardingWildlifeDiversity(WD)andFloraDiversity(FD),the

RegionalLawNo.10ofMarch2008allowsthespecificationand

quantificationofendangeredspecies attheprovinciallevel.The

regulationliststhefaunaandflorathatarethreatened.Therangeof

threatenedspecieshasbeentestedandidentifiedbytheRegional

CentreofMonteBarroAutochthonousFloraCentre(CFA).CFAis

anexperimentalstationoftheLombardyregionthefundamental

objectiveof which is topromote actionsthat ensurethe

avail-abilityofnativeplantscompatible withtheLombardyterritory.

Thespeciesforwhichinrecentyearstherehasbeennocertainty

regardingtheirexistencehavenotbeenincludedinthestudy(CFA,

2008).

TheAirQuality(AQ)indexhasbeencalculatedonthebasisofa

partialvalueforeachofthefollowingairpollutants:PM10,carbon

monoxide(CO),nitrogendioxide(NO2),sulfurdioxide(SO2)and

ozone(O3).Thus,theAirQualityindexhasbeenmeasuredbythe

followingequation:

AQ= 100×PC

PL

whereAQ=AirQualityindex,PC=concentrationofthepollutant,

andPL=thepermissiblelimitofthepollutant.

Theapproachadoptedinthecasestudyisbasedontheallocation

totheAQofthelowestsub-indexvaluethathasbeenadopted(EPA,

2009),asitisthemostwidelyusedapproachintheinternational

literature,mainlyinthefieldofforecasts.Thedatarequiredforthe

calculationoftheAirQualityindexwerecollectedandanalyzed

usingthemonitoringstationsofARPA Lombardia(ARPA,2011),

theRegionalAgencyforEnvironmentalProtection.

TheLandUse(LUC)ofthestudyareahasbeenassessedthrough

theDUSAF2.1andCorineLandCoverdatabase,whichallow

identi-fyingandmonitoringthecharacteristicsoflandcoveranduse.The

territoryisarticulatedandrepresentedby5mainclasses(Class1:

Artificialareas,Class2:Ruralterritories,Class3:Forestsandnatural

areas,Class4:Wetlands,Class5:WaterBodies).Thepercentageof

naturalsoilinthisstudyhasbeencalculatedforeachprovince.The

fiveabove-mentionedclasseshavebeencombinedwithreference

tothedegreeofthesoilnaturalness,definedbythepresenceof

humanactivitiesandtheconsequentmodificationoftheterritory

incomparisontoitsoriginalandnaturalcondition.

Thefollowing3classesderivefromthecombinationofthefive

previous:

• Populatedareas(Class1):areaswherehumanpresencehas

dras-ticallychangedtheoriginallayoutofthearea.

• Seminaturalareas(Class2):agriculturalareaswhereintensive

cultivationofthesoilprevailsoverthenaturalcomponent.

• NaturalAreas(Class 3,4,5): areasthatare theclosesttothe

naturalconditionoftheland.Intheseareas,itisexpectedthat

biodiversityishigh.

TheSurfaceWaterQuality(SWQ)hasbeenevaluatedonthe

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244 A.Oppioetal./LandUsePolicy43(2015)239–247

Fig.4.Levelofvulnerabilityforeachenvironmentalandsocio-economicfactorattheprovincelevel.

drainagesystemattheprovinciallevel(accordingtothe

classifi-cationofthecoverageofsewerageservicesintheenvironmental

authorities–theATOorAmbitoTerritorialeOttimale–that

man-agepublicservicessuchaswaterandwastedisposal).Themethod

ofpurificationisappliedtoallmunicipalitieswithmorethan2000

inhabitantequivalents.Thedataofthemunicipalitiesthatbelongto

aprovincewerecollectedforagivenprovincialwaterquality.The

degreeofwastetreatmentisapercentageoftheprovincialload.

ThedataextractedbytheFirstReportonInfrastructure(Regione

Lombardia,2008)refertotheyear2007.

SocialSecurity(SS)hasbeenconsideredfortheQualityofLife

Index,calculatedeveryyearbyIlSole24Ore,anItalianfinancial

daily,foralloftheItalianprovincesonthebasisofsixthematicareas

(thestandardofliving,servicetopeopleandenvironment,

busi-nessandlabour,publicorder,population,facilitiesandactivities

forleisure).

Table2

Measurementofthevulnerabilityvalueofeachcriterion.

Provinces WD FD AQ LUC SWQ SS Pp Ep Edu

VARESE 0.33 0.17 0.46 0.56 0.80 0.89 0.33 0.88 0.64 COMO 1.00 0.53 0.85 0.73 0.10 0.38 0.20 0.00 0.67 LECCO 0.39 0.42 0.26 0.73 0.20 0.77 0.18 0.30 0.70 SONDRIO 0.44 0.38 0.00 1.00 0.00 0.05 0.00 1.00 0.62 BERGAMO 0.28 0.43 0.43 0.62 0.20 0.41 0.17 0.28 1.00 BRESCIA 0.67 1.00 0.59 0.56 0.80 0.21 0.10 0.25 0.99 MILANO 0.22 0.15 0.84 0.05 1.00 0.00 0.93 0.62 0.00 MONZAEBRIANZA 0.22 0.15 1.00 0.09 1.00 0.00 1.00 0.61 0.00 PAVIA 0.56 0.05 0.31 0.15 0.80 0.86 0.06 0.63 0.63 LODI 0.06 0.05 0.48 0.03 0.20 1.00 0.11 0.85 0.62 CREMONA 0.00 0.05 0.53 0.00 0.00 0.67 0.07 0.26 0.69 MANTOVA 0.11 0.00 0.52 0.00 0.20 0.32 0.06 0.53 0.84

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TheindicatorforPopulation(Pp)isdensity(ISTAT,2012).

Den-sityindicatesthenumberofinhabitantslivinginagivenarea;inour

case,thereferenceunitistheprovince.Themeasureisexpressed

ininhabitantspersquarekilometre(inhab./km2).

The unemployment rate (Ep) has been defined as the ratio

betweenthepopulationaged15andabovewhoareinsearchof

employment.TheISTATLabourForceSurveyisthemainsourceof

statisticalinformationonthelabourmarket.Thedatarefertothe

year2012.

TheindicatorforEducationsystem(Edu)hasbeencalculatedas

thepercentageofresidentswithqualificationsofsecondaryschool

andbeyond(ISTAT,2001).

Table2displaysthevulnerabilityvaluesforeachcriteriaatthe

provincelevelintheLombardyregion.

Theoutputsofthevulnerabilityassessment havebeen

orga-nized into thematic maps for the purpose of providing a

comprehensiveoverviewoftheenvironmentalandsocioeconomic

stateoftheLombardyregion(seeFig.3).

Results

AsrepresentedbyGraph1,themajorityoftheprovinceshave

a VIvaluethat is abovetheaverage. In thehigherpositions of

therank, there aretheprovinces ofBrescia (VI=1) and Varese

(VI=0.96),whileinthelowerpositions,thereareLodi(VI=0.39),

Mantova(VI=0.11)andCremona(VI=0).Theothersexhibit

val-uesthatrangefrom0.42to0.62(Sondrio,Milano,Bergamo,Lecco,

MonzaeBrianza,Pavia).

Althoughthedistributionofvaluesappearsquitehomogeneous,

theanalysisofeach vulnerabilitycriteriaindicatesavaried

pic-ture.The radar charts highlight theweaknessand strengths of

each province and their degree of intensity (see Fig.4).Apart

fromthetwoclustersofprovinces–Mantova/Cremona/Lodiand

Milano/Monza Brianza – for which the vulnerability interests

exhibitthesameaxiswithacomparablelevelofimportance,the

differentshapeassumedbytheradarchartsoftheotherprovinces

revealsthepeculiarityoftheterritoryanalyzed(seeFig.4).

Graph1.TheVulnerabilityIndexineachprovinceoftheLombardyregion.Theblack lineindicatestheaveragevalueoftheVI(0.54).

Inthemajorityoftheprovinces,thevulnerabilityishigherfor

thegroupofenvironmentalfactors(WD,FD,LUC,SWQ,AQ)thanfor

thesocio-economicones(Ep,Pp,Edu,SS),exceptfortheprovinces

of Lodi,Mantova andCremona,although theruralareasarean

importantpresence.

Furthermore,astheLandUsecriteriontakesintoaccountthe

percentageofnaturalareas,thevulnerabilityassessmentneglects

thatagreatpartofthoseprovincesisoccupiedbyintensive

agri-culture,whichshouldbeconsideredasmuchasthevulnerability

factor(Mazzocchietal.,2013).Mountainareas(forinstance,inthe

provinceofSondrio),aswellastheagriculturallands,seemmuch

lessvulnerablethanhighlyurbanizedprovinces.Agriculturalareas

arenotsubjecttoaspecialprotection.Onlyafewspecificareas

areincludedinagriculturalparks(e.g.,theSouthMilan

Agricul-turalPark),whichdonothavethelevelofprotectionofnatural

parksandthereforedonotaffecttheVI;however,thisdefinition

couldleadthepolicymakerstoidentifythemaspotentialareasof

developmentandthereforeasasuitable locationforplantsand

infrastructure.

Figs.5and6. Numberoflocalconflictsanddegreeofvulnerability.Typologiesofconflictsanddegreeofvulnerability. Source:Authors’elaborationoftheARISdata.

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246 A.Oppioetal./LandUsePolicy43(2015)239–247

Therefore,thevulnerabilityvalueoftheLandUsecriterion,even

ifequal,doesnothavethesamemeaningforalloftheprovinces.

Thisisapitfalloftheassessmentmethodologythatshouldbesolved

forthepurposeofprovidingmorerobustresults.

Inadditiontothedegreeofvulnerabilityattheprovincelevel,

localconflictscausedbythedevelopmentofnewinfrastructureand

plantshavebeenconsidered(Nimby®Forumreport2012).

Throughasystemofmediamonitoring,thePermanentMedia

ObservatoryoftheNimbyForumsurveysthenewsrelatedto

ter-ritorialdisputes,anditcreatesaninventoryoftheplantsunder

opposition. The data are analyzed and discussed, providing an

updatedoverviewofthephenomenonandanannualreport.

ThelatestNimby®Forumreportindicatesthatin2012,the

num-berofplantsandinfrastructurescontestedatthenationallevelis

354(nearly7%higherthaninthepreviousedition).IntheLombardy

region,thereare54disputesagainstnewfacilities(infrastructure,

powerplants,pipelines,landfillorbiogasplantsandother).

Toexploretherelationshipbetweenconflictsandvulnerability,

theoppositionhasbeengroupedinto5categories(1.

Infrastruc-ture: mainly highways, ring roads and roads, as well as the

expansionof the airport of Malpensa;2. Energy plants:power

plantsandhighvoltagelines;3.Wastelandfills,centresforthe

treatmentofspecialwasteincluded;4.Incinerators;5.LNG

termi-nals)andoverlaidonthevulnerabilitymaps.

AsindicatedbyFigs.5and6,themapsprovideameansof:i)

puttingforwardahypothesisabouttheconflictsthathaveemerged

aroundthelocalizationofnewfacilitiesandthevulnerabilityof

theLombardyregionassessedattheprovincelevel;ii)addressing

questionsregardingthedrivingfactorsofvulnerabilityindifferent

provinces;iii)andinvestigatingthedegreetowhichthe

opposi-tionsdependsontheeffectiveterritorialvulnerability.

Theanalysisofthevulnerabilitycombinedwiththespatial

dis-tributionof local conflictsindicatesa relationship betweenthe

valueofgeneralvulnerability(VI)andthenumberofoppositions.

More precisely, theprovinces of Bresciaand Varese, for which

the VI value is 1 and 0.96, respectively, with a prevalence of

environmentalvulnerability,reveal thehighernumber of

oppo-sitions(10–11)thantheprovinceof Bergamo,forwhich theVI

value is 0.54. A lower number of conflicts is observed in the

provincesofSondrio(VI=0.42),Lodi(VI=0.39),Cremona(VI=0.11)

and Mantova (VI=0).Conflicts due to opposition to

infrastruc-ture and electrical systems are the most popular among the

provincesoftheLombardyregion.Other typologiesof conflicts

do not seem to be influenced by the degree of vulnerability

(Fig.6).

Discussionandconclusions

ThefirstoutputsofthisresearchindicatethattheVIprovides

afunctionalclassificationoftheterritories.Itcouldeffectivelybe

usedtoimprovedecisionsaboutthedevelopmentoffacilitiesand

tofairlydistributethecostsandbenefitsbothamongpublicinterest

andprivateprofitandamongpresentandfuturegenerations.The

syntheticinformationgivenbytheVImakesitpossibletocompare

andrankdifferentterritoriesaccordingtotheirdegreeof

environ-mentalandsocio-economicvulnerability.Thevulnerabilitymaps

representadditionalknowledgethatplannersshouldusefor

bet-terunderstandingthebasisoflocalconflicts.Atthesametime,they

canbeconsideredaneutralscenario,whichtheimpactscausedby

thenewfacilitiesmightchange.

With regard to the location of the conflicts, significant

dif-ferencesare not detectable,but thespread of local opposition

correspondstoalow willingnessofthecommunity toaccept a

changeintheirutilityduetothechangesinlandusethatcause

negativeexternalities.

Althoughthe conflicts shouldbe proportional tothedegree

of territorial vulnerability as has beenposited by theresearch

question,theoutputsofthisanalysisdenythisassumption.Local

disputesseem nottobeaffectedbyvulnerabilityand risk.

Fur-thermore,it must betakeninto consideration thatthis type of

proportional relationship has not emerged because the Nimby

Forumdatabasedoesnotanalyzetheriskforeachtypologyofthe

facilitiesandconsequentlytheriskperception.Nevertheless,itis

wellacknowledgedthatthereissubstantialvariationamongthe

individualperceptionsofimpacts,suchastheenvironmentaland

healthimpactsandtheeffectsonpropertyvaluesandpublicsafety

(Schively,2007).

Futuredevelopmentsintheresearchwillrequirebalancingthe

conflictimportanceaccordingtothedegreeofthespecificriskof

thedifferentinfrastructuresandplantsunderopposition.

Finally,ifthecriteriaandindicatorsthatconstitutetheindex

arewidelysharedand supportedbytheliterature,weightingis

a subjectofmore attention.Theresultsdiscussedin thispaper

havenotdeliberatelycontemplatedtheweightingoftheVI.The

weightassignmentcouldsupporttheanalysisofthestateofa

ter-ritoryinamoredynamicwaybytakingintoaccounttheeffects

ofpolicymeasuresregardingfacilitydevelopmentwiththeaidof

vulnerabilityassessment.Theweightingsystemshouldbedefined,

on the one hand, by the measurement of the specific risk, as

alreadydescribed,and,ontheotherhand,bytheinvolvementof

localcommunitiesandstakeholders.Thepublicengagementinthe

decision-makingprocessescouldbeenvisagedasanopportunity

tospreadknowledgeandawarenessaboutthevulnerabilityofthe

territories.Involvingtheperceptionsandprioritiesofthepublic

beforethedefinitionofthedevelopmentoptionscouldprevent

theadversepositionstakenagainstfutureprojectsthatareviewed

asunfairandunequal.Fromthisperspective,anunderstandingof

territorialvulnerability,groundedinenvironmental,economicand

socialcriteria,wouldseemtohelpdefinethealternativeprojects

beforethedecision-makingprocesshasbegun.

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