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Apreliminaryassessmentof
ImportantAreasforPonds(IAPs)
inthe
MediterraneanBasinandAlpineArc
TechnicalReport
GarganoandTremitiIslands,ItalyLacsdesGorgesduDorondeTermingnon
©DrGuiseppeAlfonso France
©http://www.destination‐termignon.com
CONSULTATIONDOCUMENT
Preparedforthe
EuropeanPondConservationNetwork(EPCN)
by
NaomiEwald1,PascaleNicolet1‐2,BeatOertli3ValentinaDellaBella2,LailaRhazi4,Anne‐Sophie
Reymond3,EliseMinssieux3,Er‐riyahiSaber5,MouhssineRhazi6,JeremyBiggs2,NicolaBressi2,Regis
Cereghino2,PatrickGrillas2,ThomasKalettka2,AndrewHull2,OlivierScher2andLauraSerrano2.
1PondConservation:TheWaterHabitatsTrust,c/oOxfordBrookesUniversity,GipsyLane,Oxford
OX30BP,UnitedKingdom
2EPCN,EuropeanPondConservationNetwork
3UniversityofAppliedSciencesWesternSwitzerland,hepia‐technology,architectureandlandscape
‐1254Jussy/Geneva,Switzerland
4LaboratoryofAquaticEcologyandEnvironment,HassanIIAïnChockUniversity,BP5366Maarif,
Casablanca,Morocco
5CEGA‐UMR«ESPACE»andUniversityofProvence,Aix‐MarseilleI,France
6DepartmentofBiology,FacultyofSciencesandTechniquesofErrachidia,MouslayIsmailUniversity,
BP509Boutalamine,Errachidia,Morocco
Thisreportshouldbecitedas:
EwaldN,NicoletP,OertliB,DellaBellaV,RhaziL,ReymondA‐S,MinssieuxE,SaberE,RhaziM,Biggs
J,BressiN,CereghinoR,GrillasP,KalettkaT,HullA,ScherOandSerranoL(2010)Apreliminary
assessmentofImportantAreasforPonds(IAPs)intheMediterraneanandAlpineArc.EPCN.
Thisworkispartoftheproject“PromotingpondconservationinEuropeandtheMediterranean
region(ProPond)”.FundingfortheProPondprojectwasprovidedbytheMAVAfoundation.
EuropeanPondConservationNetwork(EPCN)
c/oHepia
UniversityofAppliedSciencesWesternSwitzerland
1254Jussy/Geneva
Switzerland
www.europeanponds.org
ACKNOWLEDGEMENTS
ThanksmustgotoallthecontributorswhohavevolunteeredtheirtimetoidentifyandreviewIAPs.
TheyarelistedinfullinAppendix1and2.
OVERVIEW
TheImportantAreasforPonds(IAPs)conceptwasdevelopedtoraiseawarenessofgeographic
regionsthatsupportpondsofnationalorinternationalbiodiversityimportance,andhelpfocus
strategiesforpondmonitoring,protectionandappropriatemanagementandcreation.
Pondsarevitallyimportantforfreshwaterbiodiversityandparticularlyrecognisedassteppingstone
habitats.Theyalsoprovidearangeofecosystemservicesandhavebeenusedforcenturiesbylocal
communities.PondsandpondnetworksareabundantacrossEuropeandNorthernAfrica,inspiteof
significantlosses,butarenotadequatelyprotectedbycurrentlegislationevenwithintheEuropean
legislativeframeworkfornatureconservationandwatermanagement.Theinformationgathered
duringtheidentificationofIAPSwillbeusedtoencouragebetterprotectionmeasuresforpondsat
theregional,nationalandinternationallevel,andtheirinclusioninbiodiversityandwaterprotection
strategies(e.g.WaterFrameworkDirective,RiverBasinManagementPlans).
InordertoachievegreaterprotectionforpondsinEuropethereneedstobecoordinationbetween
countries.TheEuropeanPondConservationNetwork(EPCN),aspartoftheProPondProject
(PromotingPondConservationinEuropeandtheMediterraneanRegion,aprojectsupportedbythe
MAVAfoundation),hasbegunthisworkbyconcentratingontwobiogeographicalregions–the
MediterraneanBasinandtheAlpineArc.
SelectionofIAPswasbasedonasetofcriteriaincludingthepresenceofspeciesorhabitatsof
conservationimportance,ponddensity,andtheirsocio‐economicimportance(providingthisdidnot
underminetheirbiodiversityvalue)andotherfactorssuchasimportantassemblagesofspeciese.g.
dragonfliesandmacrocrustaceans.IAPswereidentifiedusingbothGIStechniquesandexpert
knowledgefromawiderangeofpondworkersincludingbothresearchersandpractitioners.
Forthisfirstanalysis,140proposedIAPs(pIAPs)havebeenidentifiedintheAlpineArc(30pIAPs)
andintheMediterraneanregion(110pIAPs),thelatterincludingsitesbothfromNorthernAfrica
andtheMiddleEast(28pIAPs)andfromEurope(82pIAPs).AprofileofeachIAPhasbeenproduced
withinformationonits(i)location,(ii)biodiversity,historicalandsocialvalue,and(iii)threats.
IntheMediterraneanbasin,pIAPshavebeenidentifiedin17countriesinSouthernEurope,North
AfricaandtheEasternMediterranean.TheselectedpIAPsreflecttheheterogeneityofpondsites,
andrangefromindividualpondsinSpainsupporting18speciesofEuropeanconservation
importancetopondnetworksinItalyknowntocontainover60speciesofEuropeanconservation
importance.ManyareasqualifiedasIAPsbecauseofhighponddensity(e.g.over15pondsperkm2
inGreece)whereasothersqualifiedbecausetheycontainedmanypondsscatteredoverlargeareas
(e.g.1613pondsover200000hainMorocco),representingadispersedbuthighlysignificant
freshwaterbiodiversityresourceintheregion.Thesocio‐economicvalueofpondswasalso
recognisedintheiridentificationaspIAPs:somesuchasinIsraelshowevidenceofcontinuoususe
sincetheRomanoccupation.
TemporaryPondsinAltPalancia,Spain
ManyIAPs,particularlyinNorthernAfricaandthe
EasternMediterraneanhavenocurrent
protection,inspiteofthehabitatsandspeciesof
conservationconcerntheysupport,andallare
undersignificantthreatfromtheincreasing
pressuresofagricultureanddevelopment.Raising
theprofileofthesesitesthroughdesignationas
IAPswillhelptosecuretheirprotectionandfuture
sustainablemanagement
IntheAlpineArc,atotalof30pIAPswere
proposedinthefourmaincountrieswhichmade
uptheregion.Somehadexceptionallyhighpond
densities(e.g.pIAPswithover30pondsperkm2
intheFrenchAlps),whereasothersinthesameregioncompriseasinglepondwithimportant
assemblagesofspecies.Pondnetworkswerealsoidentified:someextendedoverlargeareas,
exceeding2000hainItaly,whilstothers(e.g.inAustria)wereconcentratedwithinanareaofless
than20ha.
ThemajorityofpIAPsintheAlpineArccontainedspeciesofEuropeanconservationimportancebut
alsohighaltitudestenothermalspecies.However,thesealpinepondsarenotwellrepresentedinthe
listofpondtypesgivenundertheHabitatsDirectiveleadingtoalackofdesignationwithinthe
Europeanlegislativeframeworkofprotectedsites.Theidentificationofnetworksofpondsinthe
AlpineregionasIAPswillprovidegreaterrecognitionoftheirimportancetobiodiversityatan
internationallevel.Thisisparticularlyrelevanttohighaltitudesites,astheyareundersignificant
threatfromclimatechange,anissuewhichrequirescooperationandimplementationof
conservationinitiativesataninternationallevel.IAPsintheAlpineArcalsodemonstratethecultural
importanceofponds.Manyhavealonghistoryofuseparticularlywithinthetraditionalpastoral
economyoftheregion.Morerecentlypondnetworksareprovidingavaluableresearchand
educationaltoolforboththescientificcommunityandthewiderpublic.
ThisreportisapreliminaryassessmentofIAPsintheMediterraneanandAlpineArcregion.
ProposedIAPs(pIAPs)willbereviewedthroughapublicconsultationprocessandeitheracceptedas
afullIAP,modifiedordeclined.ThepIAPsidentifiedaspartoftheProPondProjectwillbepublished
ontheEPCNwebsite.Thisshouldensurethattheinformationisrapidlydisseminatedtopond
conservationpractitionersandturnedintopositiveactiontoprotectandenhancethepond
biodiversityresource.
ThepIAPspresentedinthisreportincorporatethehighqualitypondssofarknown:weanticipate
that,astheprofileandknowledgeofpondsgrows,aidedbytheIAPprocessitself,considerably
morehighqualitypondwillbefoundintheseregionsthanhavecurrentlyidentified.TheEPCNwill
nowcontinuetocoordinateandfacilitatethiswork,buildingonthemomentumoftheProPond
project.Akeyroleofthenetworkanditsmembersisnowtodisseminatetheinformationpresented
hereaswidelyaspossibleaspartofaconsultationprocess,butalsotoinforminternationaland
nationalpolicymakers.
CONTENTS
1.INTRODUCTION..............................................................................................................................................1
1.1Theimportanceofponds........................................................................................................1
1.2Pondprotection.......................................................................................................................2
1.3Ponddefinition........................................................................................................................3
2.IMPORTANTAREASFORPONDS(IAP)...........................................................................................................4
2.1IdentifyingIAPs........................................................................................................................4
2.2Selectioncriteria......................................................................................................................5
2.3IAPselectionprocess...............................................................................................................7
3.THEMEDITERRANEANBASIN.........................................................................................................................
8
3.1Spain......................................................................................................................................10
3.2Portugal.................................................................................................................................12
3.3France....................................................................................................................................14
3.4ItalyandMalta.......................................................................................................................16
3.5BalkanStatesandCyprus.......................................................................................................18
3.6Morocco.................................................................................................................................20
3.7AlgeriaandTunisia.................................................................................................................22
3.8MiddleEast............................................................................................................................23
4.THEALPINEARC...........................................................................................................................................24
4.1France....................................................................................................................................26
4.2Switzerland............................................................................................................................27
4.3AustriaandItaly.....................................................................................................................29
5.RecommendationsandConclusions............................................................................................................30
6.References...................................................................................................................................................31
Appendix1ListofcontributorstotheMediterraneanIAPs............................................................................32
Appendix2ListofcontributorstotheAlpineArcIAPs....................................................................................34
Appendix3SpeciesassociatedwithpondsintheMediterraneanandAlpineArc..........................................35
Appendix4PondassociatedhabitatsandspeciesprotectedundertheHabitatsDirective...........................41
1
LacdesSaisies,France
1. INTRODUCTION
1.1 The importance of ponds
Pondsareimportantfreshwaterhabitatsthatplayasignificantroleinmaintainingfreshwater
biodiversityandprovideasignificantfreshwaterresource.Thereareover10millionsmallwater
bodies(lessthan10ha)inEurope,whosetotalsurfaceareaaccountsforalmost30%ofall
permanentsurfacewater(Oertlietal.2005).ThisisinspiteofsignificantlossesinsomeEuropean
countries‐upto90%inSwitzerlandandtheNetherlands,and50%inSwedenandPoland(EPCN
2008).InNorthernAfricatherearethousandsofpondsrecognisedfortheirbiodiversityvalue,but
underincreasingpressurefromurban,agriculturalandindustrialdevelopments(Rhazietal.2006).
Pondshavehighecologicalinterestbecauseofthefloraandfaunatheysupport,including
amphibians,invertebrates,vascularandlowerplantsandmicro‐organisms,withmanyprotected
specieswhicharethreatenedatbothnationalandinternationallevels.Thevalueofpondsalsolies
inthevariednetworkofhabitatsthattheyprovide,andataregionallevelpondsareoftenmore
importantinmaintainingfreshwaterbiodiversitythanothermoreextensivefreshwaterhabitats
(Williamsetal.2004,Daviesetal.2005).Theyalsoprovideconnectivityacrosslandscapesandare
recognisedassteppingstonesvitalforthedispersalofspecieswithinlandscapes(Cereghinoetal.
2008).Whenanumberofpondsarelocatedincloseproximitytheirbiodiversityvalueincreasesstill
further,allowingspeciestoexistasmetapopulations,strengtheninggeneticexchangeandbuffering
populationsfromextinctionevents.
Pondsareoftenofhighhistoricalandeconomicvalue,usedinagriculture,industryandasasource
offreshdrinkingwaterforbothlivestockandlocalpopulations.Pondsarealsousedforrecreation
andhaveanintrinsicvaluetomanypeoplebecauseoftheassociationbetweenpeopleandponds
forthousandsofyears.Therelationshipbetweenpeopleandpondsprovidestheopportunityto
engagewithlocalstakeholdersintheirmanagementandconservation(EPCN2008).
However,pondsarealsoavulnerablehabitattype.Theyexperiencealloftheimpactsthataffect
otherfreshwaters,andadditionallocalpressuresspecifictosmallwaterbodies.Theseinclude
changestofarmingpractices,includinglossof
traditionalmethodstomoreintensivetechniques,
changestothehydrologicalregimefromdrainageand
abstraction,developmentfromurbansprawlandroad
infrastructure,tourismandthecolonizationofponds
byinvasivespecies.Moregenerally,pondsare
especiallyvulnerabletopollutionstressesbecause
theirsmallsizegivesthemlimitedbufferingcapacity
comparedtoriversorlargerlakes.Asaresultof
widespreaddestruction,pondnumbersarenow
probablyclosetoanalltimelowacrossEurope
(Hull1997).
2
However,inspiteofthelossesandthreatsfacingponds,theyalsoprovideimportantopportunities
forconservingbiodiversity.Theirsmallsizeandhighlevelsofheterogeneitymakethemeasyto
createandmanageinalmosteveryhabitattype.Theyprovideimportantecosystemservicesand
connectwiththesustainablemanagementofenvironmentsatlocal,regionalandgloballevels.Inthe
rightdensityandifstrategicallyplaced,theycanprovidealinkbetweenimportantareasof
biodiversityaswellasbeinganimportantbiodiversityresourceintheirownright(EPCN2008).
Becausethebiodiversityinterestofpondsisoftenwidelygeographicallydistributed,andbecause
pondsfaceanexceptionalrangeofthreats,protectingthemisachallengeforpolicymakersand
managers.Pondsaregenerallytoosmalltofitthestandardmodelofsite‐basedprotectionandthey
donotfitthestandardmodelofconsent‐basedprotectiondesignedtoprotectwaterbodieslike
lakesandriversfromindustrialdischarges.Despitemuchinterestinthemanagementofcatchments,
effectiveprotectionofpondsthroughlandscapewidemeasuresisrarelyachieved(Section1.2).For
allthesereasons,newmodelsofprotectionarerequiredifwearetomaintainthebiodiversityand
historicalvalueofthesesmall,vulnerable,freshwaterhabitats.
TheEuropeanPondConservationNetwork(EPCN)wasestablishedin2004toaddresstheseissues,
andalreadyincludesover150membersfromalmosteverycountryinEuropeandNorthernAfrica.
ThemissionoftheEPCNistopromotetheawareness,understandingandconservationofpondsina
changingEuropeanlandscapeanditspondprotectionstrategyissetoutinthePondManifesto
(EPCN2008).TheEPCN,fundedbytheMAVAFoundation,hasundertakentheProPondprogramme:
PromotingPondConservationinEuropeandtheMediterraneanregionasitsfirstmajorprogramme
ofworktoimplementaEuropeanconservationstrategyforponds.Aspartofthis,theEPCN,in
collaborationwithotherpondworkers,hasbeguntheprocessofidentifyingImportantAreasfor
Ponds(IAPs)intheMediterraneanandAlpineArcregions,providingaprotocolwhichcanbeapplied
totherestofEurope.
1.2 Pond protection
IntheEU,oneofthemosteffectivemeasurestoensurehabitatprotectionisthedesignationofa
sitewithinthelegislativeframeworkofprotectedsites.Twopiecesoflegislationareparticularly
relevanttoponds:theHabitatsDirective(92/43/EEC)andtheWaterFrameworkDirective
(2000/60/EC).UndertheHabitatsDirective,memberstateshaveinternationalobligationsfora
rangeofspeciesfoundinponds.Annex1oftheDirectivealsolistsseven“habitatsofhigh
conservationimportance”thateitherpartlyorwhollyincludeponds(Appendix4).Inaddition,ponds
arenotedinArticle10asstepping‐stonehabitats,whichmemberstatesneedtoconsiderintheir
planningpoliciestoencourageecologicalcoherenceoftheNatura2000network.
TheotherpieceofEUlegislationrelevanttopondsistheWaterFrameworkDirective(WFD),whichis
intendedtoprotecttheecologicalqualityofallwatersinacatchmentcontext.However,most
nationaladministrationshaveadoptedalowersizelimitof50hectaresfortheidentificationof
standingwaterbodiestobemonitoredaspartoftheWFDimplementation.ThereforeEurope’smost
powerfulpieceofwaterlegislation,ascurrentlybeingimplemented,islikelytobringlittleprotection
forponds.
3
PresidentialEstateofCastelporziano,Italy
OutsideoftheEUlegislativeFramework,pondscanreceivesomeprotectioniftheyareonsites
designatedthroughinternationallaworinitiatives.Ofthese,theEmeraldNetworkinitiative,
launchedbytheCouncilofEuropeundertheBernConvention,ispotentiallythemostimportantfor
ponds.Thisnetworkidentifiesareasofspecialconservationinterestandrepresentsthedefacto
extensionofNatura2000sitestonon‐EUcountries,althoughitisnotlegallybinding.The
concentrationofMediterraneanTemporaryPonds,asdefinedbyNatura2000,withinNorthern
AfricashouldqualifymanysitesidentifiedaspartoftheIAPprocessforinclusionintheEmerald
Network.Severalotherinternationaldesignationsmayalsoaffordpondsitessomeprotection,
althoughdesignationstendtobenon‐legallybinding,includinge.g.BiosphereReserves(UNESCO)
andImportantAreasforBirds(IBAs).
TheIAPprocesswillhelpincreaseawarenessoftheimportanceofthepondresourcegenerally,and
ofIAPpondsitesinparticular.Itcanbeusedtoencouragebetterprotectionmeasuresforthese
sitesattheregional,nationalandinternationalscale,andtheirinclusioninbiodiversityandwater
protectionstrategies.IAPsshouldbeconsideredinallstrategicplanswhichaimtoachievethe
sustainablemanagementandprotectionofbiodiversityatregional,nationalandlocaladministrative
levels.
1.3 Pond definition
Inordertoprotectaresourceitisnecessarytodefinethehabitattype.Pondshavebeenpartof
humancivilizationforthousandsofyearsbuttheirvariabilityintypeanddifferencesinusehaveled
tomultipledefinitionsbasedonvariousaspectsoftheirsize,depth,typeofwatersupply,use,
geographicallocation,formation,andwaterquality(seeBiggsetal.2005forareviewofpond
definitions).
TheEPCN(EPCN2008)hastakenabroaddefinitionofwhatconstitutesapondwhichwillapply
acrossadministrativeboundariestoincludethefullrangeofpondhabitattype.
“Atemporaryorpermanentstandingwaterbodybetween1m2and5hectares
insurfacearea.”
4
2. IMPORTANTAREASFORPONDS(IAP)
2.1 Identifying IAPs
TheImportantAreasforPonds(IAP)conceptwasproposedanddevelopedbyPondConservationto
raiseawarenessofgeographicregionsthatsupportpondsofnationalorinternationalbiodiversity
importance.TheprojectwassuccessfullypilotedinWales,UK(Nicoletetal.2007)andhassince
beenappliedtotwootherregionsintheUK.Identifyingareasthatareimportantforbiodiversityisa
conceptwhichhasbeenappliedattheglobalscale‐BiodiversityHotspots(Myersetal.2007),within
Europe‐KeyBiodiversityAreas(Edgeretal.2008)andfordifferenttaxonomicgroups(Areasof
Importance,includingbirdsandplants).
Aswiththeponddefinitionabove,theEPCNhasagreedabroaddefinitionforIAPswhichcanbe
appliedtoarangeofgeographicalscaledependingonthecharacteristicsofthepondsofinterest.
“AnIAPisageographicalareawhichsupportsapondsiteornetworkofhighbiological,
socialoreconomicimportance.”
TheaimofIAPsistoidentifynetworksofthemostimportantpondsandtheirbiodiversity.These
areascanthenbeusedtohelpfocusstrategiesforpondmonitoring,protectionandappropriate
managementandcreation.Specifically,knowledgeofIAPswill:
• HighlightIAPsforpractitioners(includingconservationagencies,governmentauthoritiesand
non‐governmentalorganisations),creatingabetterunderstandingandrecognitionofthepond
resource.
• Increaseawarenessoftheimportanceofspecialandoftenoverlookedpondtypes(e.g.
temporaryponds),andthespeciestheyprotect.IAPscanalsobeusedasaguidetobest
practiceinpondconservationandmanagement.
• Helptoprotectpondnetworksandpreventfragmentationoffreshwaterresources.Sitesshould
beviewedaspartofthewiderlandscape,withmanagementseekingtoprotectandextend
pondhabitats.
•Informregulatoryagenciesofareaswherepondsshouldbegivenparticularprotection.Thiscan
beachievedbyusingexistinglegislationmoreeffectively,influencingpolicydevelopmentand
integratingIAPsinlocaldevelopmentstrategies.
Giveasenseofownershiptolocalcommunitiesandhelptoensurethattheprofileofpondsis
raisedinthepublicconsciousness.
5
2.2 Selection criteria
Theselectionofimportantareasisbasedonasetofcriteriatoprovidearobustjustificationfortheir
designation.Thesecriteriacanbequalitative,basedonthepresenceofprotectedhabitatsorthe
presenceofprotectedspecies,ortheymaybequantitative,forexample,thesizeofanareaor
numberofhabitatunitswithinagivenarea.Subjectivemeasuresalsoincludetheimportancewhich
localcommunitiesgivetothepondresource.Intheabsenceofpublisheddata,pondpractitioners
canalsouseexpertpersonalknowledgetoidentifyimportantpondswithinaregion.
TheEPCNhasdevelopedthefollowingfivecriteriatoidentifyIAPs(Table1):
Aregionwithahighdensityofpondsinterconnectedatthelandscapelevel(pondnetwork).
AmethodologytoidentifypondnetworksusingGISandremotesensingtechniqueswasdeveloped
inSwitzerland(Reymond2008,Minssieux2008)andhasprovedtobeaneffectivetechniquein
identifyingpondclustersintheAlpineArcandinthesomepartofMorocco.However,remote
sensingtechniquesareoftenlesseffectiveforpondswhicharesmallinsize,temporary,within
densevegetationorhiddenundertrees.Insuchcases,andwheredetailedremotesensinganalysis
wasnotpossibleforotherreasons,andintheabsenceofsetthresholdfiguresonponddensity,
expertknowledgeandtheuseofothercriteriawereusedtoidentifypondnetworks.
OneorseveralHighQualityPond(s).AHQPisapondwithahighbiologicalvaluebecauseofthe
rarityofhabitatandspeciestheysupport.
PondssupportingpopulationsofEuropeanprotected,rare,threatenedorendemicspeciesqualifyas
aHQP.AlistofallspeciesusedintheidentificationofIAPshasbeenincludedinAppendix3.
Identificationofpondsbasedonspeciesreliesongoodqualityandaccessibledata,somethingwhich
islackingformanyofthetaxonomicgroupsassociatedwithpondsinmanycountries.Thebest
availabledatahasbeencollatedforonlyafewgroupsincludingplants,amphibians,Odonataandin
theMediterranean,macrocrustaceans.
PondswhichsupporthabitatsofEuropeanimportancealsoqualityasHQPs(aslistedinAnnex1of
theHabitatsDirective).ThehabitatsusedintheidentificationofIAPsarelistedinAppendix4.In
NorthernAfricaandtheMiddleEast,thepresenceofAnnex1habitatswasalsousedtoassesssites,
asintheEmeraldNetwork.
Placesrecognisedfortheirpresentorhistoricalsocialinterest(e.g.placesoftourism,swimming
ponds,fishfarmingpond,recreationalanglingpools,pondsrecognisedfortheirscenicbeauty,
etc.).
Ithasbeenshownthatpondswithhighsocio‐economicvalueareoftenmanagedmoresustainably
thansiteswhichareundervaluedorneglected.InFrancearegistryexistsforsiteshaving‘artistic,
historical,scientific,legendaryorpicturesquevalue’.Switzerlandhasafederalinventoryofnatural
andculturalheritage.ThepondswithinMoroccoarerelieduponbylocalcommunitiesforfresh
waterforlivestockandvillagers.Itwasimportanthoweverthattheseusesremainedcompatible
withthebiodiversityimportanceofthesite.
6
Otherqualitativeandquantitativemeasures.
AlthoughitisdesirabletoselectIAPsusingstandardizedcriteriasomeareas,whichexpertjudgment
clearlyindicatetobeimportant,lackthedatanecessarytoqualifyusingtheformalcriteria.Toavoid
theexclusionofsuchsitesIAPsmayalsobeselectedonthebasisofothercriteriabasedonexpert
knowledgeaboutasiteorregion.TheidentificationofIAPsinthiscategoryshouldincludea
descriptionofthequalifyingothercriteriawithanaimtofillinmissingdataasitbecomesavailable.
Table1summarisesthecriteriausedintheselectionofIAPs.Formoreinformationonthe
developmentofthecriteriarefertoReymond(2008)andMinssieux(2008).
Table1:SelectioncriteriaforIAPsintheMediterraneanBasinandAlpineArcregions.
Criteriatypes
Selectioncriteria
A.SiteswithahighponddensityPondcomplexesorclusterswhicharelikelytosupport
metapopulationsofpond‐associatedplantsandanimals
B.SiteswithhabitatsofEuropean
orMediterraneanimportance
HabitatslistedinAnnexIoftheHabitatDirective
C.SiteswithspeciesofEuropean
orMediterraneanconservation
importance
B.1.Siteshostingspeciesprotectedbyinternationalor
Europeanlegislation:
I. SpecieslistedinAnnexI,IIandIIIoftheBerneConvention
II. SpecieslistedinAnnexIIandIVoftheHabitatDirective
B.2.Sitehostingthreatenedspeciesatinternationalor
Europeanlevel:
I. SpecieslistedontheIUCNRedList
II. SpecieslistedontheEuropeanRedList
B.3.Siteshostingendemicspecies:
SpecieswhichareuniquetoEuropeortheMediterranean
regionandarefoundnowhereelseintheworld
B.4.Otherstatus:specieswithoutparticularstatusbut
potentiallythreatened:
I. Specieswhichsmalllocalisedpopulations
II. Relictspecies
D.Sitesofhighsocial(historical,
culturalorscientific)oreconomic
importance
Pondsiteswhichrepresentexceptionalexamplesofthesocial
oreconomicusesofponds
E.Otherselectioncriteria
PondsiteswhichdonotqualifyundercriteriaAtoDabove,but
whicharedeemedofexceptionalimportanceforotherreasons:
forexamplebecauseoftheirhighspeciesdiversityatnational
level,theirgeomorphology,etc.
7
2.3 IAP selection process
Insummary,theselectionofIAPsisathreestepprocess(Figure1)whichbeginswiththe
identificationof(i)pondsqualifyingasHighQualityPonds,basedonthepresenceofspeciesor
habitatsofconservationimportance,(ii)areaswithahighponddensity,or(iii)pondsitesof
particularsocio‐economicimportance.ThisleadstotheidentificationofproposedIAPs(pIAPs)
whicharethenreviewedthroughaconsultationprocessandtheneitherconfirmedorrejectedas
IAPs.Inpractice,ponddataarenotavailableoratleastdifficulttoaccessinmanycountries,and
expertknowledgewasheavilyreliedupontoidentifyIAPs.TheselectionofIAPsandcollationof
proposedIAPswascoordinatedwithineachregionbymembersoftheEPCN.
Figure1:TheIAPselectionprocess
AprofileofeachpIAPhasbeenproducedwithinformationonits(i)location,(ii)biodiversity,
historicalandsocialvalue,and(iii)threats.Thesesiteprofilesarecollatedinaseparatedocument
whichisavailableontheEPCNwebsite(www.europeanponds.org).Hereweprovideasummaryof
thepIAPsidentifiedineachcountrywithintheMediterraneanBasinandAlpineArc,includingamap
ofpIAPlocationsandacross‐referencetothepagenumbersofeachpIAPsiteprofileinthe
accompanyingdocument.
8
3. THEMEDITERRANEANBASIN
TheMediterraneanregionisdefinedbyitsclimate.Duringthesummeritreceivessubtropicaldry
andwarmair,whilstinthewintertheregionexperiencescyclonicmaritimestormsfromthePolar
Regions.Thisisoftendescribedasawinter‐rain,summer‐dryclimate.
Therigoursoflivinginthistypeofextremeclimatehaveresultedinahighdegreeofendemismin
thearea.Thisisreflectedinthenumberofpriorityspecies(Natura2000)recordedhere(59%ofall
priorityspeciesonAnnexII).Theclimatealsopromotestheformationoftemporaryponds.In
NorthernAfricathesearethepredominantpondtype,supportingauniqueanddiverseplantand
animalcommunity.Temporaryponds,however,donotconstituteahomogeneousgroupandvary
considerablydependingonlocalphysico‐chemicalcharacteristicssuchassoilsandsurfacearea.The
dayasofMorocco,forexample,oftenhaveasurfaceareaofseveralhectares,whereasthecupular
poolsofSicilycanbelessthanonesquaremetre.
ThepondsoftheMediterraneanregionalsohaveahugesignificanceforlocalpopulationsasa
sourceoffreshwater.InNorthAfricatheyareoftenlocatedinorneartowadis,dryriverbedswhich
onlyfillduringheavyrainfall.Thepondspersistlongerthantheriverwaterandbecomeoasesfor
grazinganimals.
ThreatstopondsintheMediterraneanregion
aresimilartothosefacedbysmallwaterbodies
everywhere,buttheirvulnerabilityisgreater.
Thepoolsareshallowandoftensmallinarea
andvolume.Thismakesthemexceptionally
susceptibletopollution,drainageand
destructionbyman.InSouthernEuropethese
threatsincludetheabandonmentofagricultural
practices,eutrophicationduetoagricultureand
inappropriatemanagement(Medailetal.1998).
Mediterraneantemporarypondsprotected
undertheEUHabitatsDirectiveincludeonlya
smallproportionofalltemporarypools:
specificallythosewhichhaveoligotrophicwater
andsupportparticularplantandinvertebrate,
mammalandbirdcommunities.Other
temporarypondsreceivelittleornoprotection
undernationalorinternationallegislation.Asa
resultidentificationofIAPsisessentialtoraise
theprofileoftheseimportanthabitatsand
ensuretheirrecognitioninwatermanagement
strategies.
MassifduBouhachem,Morocco
MalladasdelaDevesa,Spain
9
Atotalof110IAPshavebeenidentifiedintheMediterraneanregion(Figure3).Theavailabilityof
dataandlevelsofinformationtosupporttheirselectionvariedgreatlydependingonthecountry.
ForexamplethelocationofFrenchIAPswasbasedpredominantlyonliteraturereview,whilstthe
locationofpIAPsinAlbaniawasbasedonanalysisofGIStoidentifypondclusters.InMenorcaa
remarkableLIFEBASSESprojecthassurveyedandmappedthetemporarypondsonthewholeisland
providingdetailedinformationonallaspectsoftheseponds(FragaiiArguimbau2010).Thisexample
shouldbeusedasabestpracticecasestudybecauseofthequantityandqualityofMediterranean
TemporaryPondsfoundthere.
Figure2:OverviewofthelocationofpIAPsintheMediterraneanRegion.
InNorthernAfricaandtheEasternMediterraneanmanypotentiallydegradingactivitiesoccurredin
oraroundthepoolsineachoftheIAPsidentified.Manyoftheseweretheresultofagriculture
(includinggrazingandcropping),butalsoincludeddisruptionofthehydrologicalregime(complete
lossofwaterduetoabstraction,irrigation,climatechange,etc.).VeryfewpondsintheseIAPs
carriedanyformofinternationalrecognition(2IAPs)andonly25%werecoveredbyanational
conservationdesignation.IntheEuropeanMediterraneanregionthelevelofprotectionwasmuch
greater.However,interestinglythenumberofreportedthreatsfortheseIAPswasashighasthosein
Africainspiteofthelevelofprotectionaffordedtothem.
SPAIN
FRANCE
PORTUGALITALY
MOROCCO
ALGERIAMALTA
LIBYA LEBANON
EGYPT
CYPRUS
GREECE
MONTENEGRO
ALBANIA
ISRAEL
10
LavajodeAbajodeSinarcas,Spain
3.1 Spain
InSpain27pIAPshavebeenidentified.This
reflectsthecombinationofbedrockand
climate,whichresultsindevelopmentof
numeroustemporaryponds,butalsothe
numberofpondworkersinthiscountry.
Thepondssupportalargenumberof
specialistspecies,manyofwhichare
endemictothisregion.
TherewasanotabledifferenceinthepIAPsidentifiedinthisregion.Somecompriseoutstanding
examplesofhighqualityponds(e.g.DonanaandMenorca)wheredetailedinformationexistsonthe
presenceofspeciesfromawiderangeoftaxonomicgroupsandprioritypondhabitats.Projectsare
on‐goinginthesepIAPstomaintainandenhancethepondresource.ForotherpIAPs(e.g.Douro
Basin),informationexistsonthepresenceofprioritypondhabitatsbutthereisalackofinformation
undertheotherIAPcriteria.Thesesitesareunderahighlevelofthreatduetotheirlackof
recognitionandurgentactionisrequiredtoensuretheirprotection.EvenatsitessuchasDonana,
whicharedesignatedundermanyinternationalandnationalschemes,temporarypondsare
threatenedbywaterabstraction,intensificationofagricultureinvasivespeciesandpressuresfrom
tourism.ThesethreatsarecommontoallvirtuallyallMediterraneanpIAPs,illustratingtheneedto
increasetheprotectionaffordedtothesehabitats.
11
IAPcodeSitenameIAPSiteProfile
Pageno
SP01ElAbalariopondcomplex 1
SP02TemporarypondsinAltMaestrat 4
SP03TemporarypondsinAltPalancia 6
SP04BassadelCavall9
SP05Campiñasurponds 11
SP06Cardenaponds13
SP07Donanatemporaryponds 15
SP08ElPalancosopond20
SP09FuentedePiedraponds 22
SP10LaGitanillapond24
SP11LaNavapond26
SP12LaRocapond28
SP13LavajodeAbajodeSinarcas 30
SP14Lebrija‐LasCabezasponds 33
SP15LosArenalesponds 35
SP16MalladasdelaDevesa 37
SP17Menorca39
SP18RedondaorMelchorGomezpond 43
SP19SantaOlallaPonds45
SP20CompejoLagunarCarsticodeCuenca 47
SP21HoyadeBezas49
SP22Trujillanapond51
SP23VeigadePontellinares53
SP24DouroBasin56
12
Galeado,SWPortugalPonds
3.2 Portugal
AtthewesternlimitoftheEuropean
Mediterraneanbiogeographicregion5pIAPs
wereidentifiedinmainlandPortugal.These
rangedfromaltitudesof50m(Galeado)toover
2000ma.s.l.(SMiguel).ThepIAPsrangedinsize
from12.8hato3200haandcontainedoneor
morepriorityhabitatsassociatedwithor
surroundingtheponds.Somesitesalsoqualified
onthebasisofponddensitywithupto8ponds
perkm2(Malhao).
Inspiteofthislevelofbiodiversityvalueonly
onesite(SagresPonds)isaffordedprotection
underEUlegislation.Howevertheothersites
wereaffordedsomeprotectionattheNational
level.ThesepIAPsarethreatenedbya
combinationofhumanactivitiesincluding
changeinagriculturalpracticefromtraditional
grazingtointensiveagricultureandplantingof
crops,withassociateddrainageand
mismanagementofwaterresources,and
increasingpressurefromtouristdevelopments.
IAPcodeSitenameIAPSiteProfile
Pageno
PT01SMiguel65
PT02SagresPonds68
PT03Malhao71
13
PT04Galeado74
PT05VilaDo Bispo77
14
MaredeCatcheou,France
3.3 France
TheFrenchMediterraneansupportsnumeroustemporary
pools(3170*),includingsiteswhicharebothman‐made
(Roque‐Haute)andnatural(Biot)inorigin.Atotalof21pIAPs
havebeenidentifiedinthisarea,basedonthedensityof
ponds,thepresenceofprotectedplantspeciesand
identificationofprioritypondhabitats.Allthesitesincludedin
thispreliminaryassessmentareaffordedprotectionwithinthe
Natura2000network.AsinSpainmanyofthesesitesarestill
threatenedfromintensificationofagricultureand
development.
TheMediterraneanregionofFranceisunderpressurefrom
development,drainageandintensificationoflanduse.Thisis
leadingtothedegradationofpIAPsitesbecauseofisolation
andhabitatfragmentation.Thereisaneedtoimprovethe
statusofpondsinFrancethroughcollationanddissemination
ofknowledgeaboutpondbiodiversity,sustainable
managementofpondsandlegislationtoprotectthepond
resource.
15
IAPcodeSitenameIAPSiteProfile
Pageno
FR01Agde80
FR02Beziers82
FR03Capelle84
FR04Centre‐Var86
FR05Costieres88
FR06Crau90
FR07Biot93
FR08MaredeCatcheou95
FR09Massifd'Esterel98
FR10PlainedesMauresandMassifdesMaures101
FR11Camargue104
FR12Pezenas107
FR13Rodes109
FR14Roque‐Haute111
FR15StEsteveetTorremila114
FR16Vendres116
FR17Agriates118
FR18Bonifacio121
FR19CapCorse124
FR20LittoralSWCorsica127
FR21PtoVecchio130
16
PortoCaleriCoastalPonds,Italy
3.4 Italy and Malta
WithinItaly,19pIAPswereidentified.ThepIAPswerewidely
distributedacrosstheItalianmainlandandadjacentislands
andasaresultwerehighlyvariablebecauseofchangesin
topographyandtheunderlyingbedrock.Sitesrangedin
altitudefromsealevel(IsolaGrandeePantanodiSan
Teodoro)to1096ma.s.l.(MonteCarcaci).Siteareawasalso
veryvariablefromonly3ha(StagnidellaMercareccia)to125
000ha(MonteMinervaWetArea).
AllsitesqualifiedasapIAPbecauseofthepresenceofprotectedspeciesorthepresenceofa
Europeanprotectedhabitat.AsaresultalmostallwereprotectedatEuropeanlevel.TheGargano
andTremitiIslandsareworthyofspecialmentionbecauseofthenumberofprotectedspeciesand
levelofprotectionaffordedtothem,representingaveryhighqualitypondresource.Somesites
werealsoselectedbecauseoftheirhistoricvalue,forexampletheFerrararettingpoollandscape.
ThepondresourceinItalyisunderimmensepressurefromurbanization,landcoverconversion,
changesinagriculturalpracticesandtourism.Recognitionoftheirimportanceinlocalplanning
policiesisessential.
17
IAPcodeSitenameIAPSiteProfile
Pageno
IT01Albegnaplainpondscomplex 133
IT02PresidentialEstateofCastelporziano 135
IT03CirceoForest141
IT04EasternSalento144
IT05FerraraRettingPoolLandscape 148
IT06FoglinoWood152
IT07GarganoandTremitiIslands 155
IT08IsolaGrandeandPantanodiSanTeodoro 159
IT09MonteCarcaci162
IT10MonteLauro165
IT11MonteMinervawetarea 168
IT12Nardoponds170
IT13NaturalReserveofMacchiatonda 172
IT14PantanidellaDoganella 175
IT15PaludediImbutillo177
IT16PortoCalericoastalponds 180
IT17SentinaNaturalRegionalReserve 183
IT18StagniDellaMercareccia 186
IT19WesternSalento188
MAL01SanPawltat‐Targapools 191
18
SchiniasMarathonPonds,Greece
3.5 Balkan States and Cyprus
IntheEasternMediterranean,7pIAPswere
identifiedinGreeceandCyprus.Thesesites
qualifiedbecauseofthepresenceofprotected
speciesandhabitats,andallwerewithinthe
Natura2000network,withtheexceptionof
KamposKarystoupIAP.ThesepIAPswere
predominantlyinlow‐lyingareaswhichputsthem
undersignificantpressurefromhumanactivities
includingdevelopment,extensiveagriculture,
overexploitationofwaterresourcesandtourism.
However,projectsarealreadyunderwayto
protectandenhancethepondresourceinthis
regione.g.theEuropeanLifefundedproject
"ActionfortheconservationofMediterranean
TemporaryPonds”inCrete.
FortheremainingBalkanstateswithintheMediterraneanfewpIAPshavebeenproposed.This
reflectsthelackofinformationonthepondresourceinthesecountries,ratherthanthequalityof
thepondresource.Montenegrohasproposed1pIAPwhichcontainsbothprotectedspeciesand
habitats,importantassemblagesofotherspeciesandwhichcontainsahighdensityofponds.Yet
thepondsofthispIAParecurrentlyaffordedonlyNationalprotection.Othercountriesareatthe
beginningoftheIAPselectionprocess.AlbaniahasidentifiedIAPsusingGIStechniques,whilst
Sloveniahasrequestedmoreinformationontheselectioncriteriasothatitcanfeedintotheprocess
atalaterdate.
19
IAPcodeSitenameIAPSiteProfile
Pageno
MTG01Moromispond193
ALB01Albania195
GR01KamposKarystouPonds200
GR02MountOchiAreaPonds203
GR03Omalospond205
GR04SchiniasMarathonPonds208
GR05SperchiosValleyPonds210
CYP01OrokliniLakeSaltmarshPonds212
CYP02ParalimniLakePonds214
20
Chaouia,Morocco
3.6 Morocco
WithinMorocco,atotalof15pIAPshavebeenidentified.
Theserangedinsizefrom100ha(HautAtlas)to151000
ha(Mamora)andinaltitudefrom10mto770m.Allsites
qualifiedonthebasisofhabitatsofhighconservation
importance,andthepresenceofprotectedspecies.Sites
alsoqualifiedonthebasisofponddensity.Theseare
relativelylow(highdensity=0.2pondsperkm2,Haut
Atlas),reflectingthearidnatureoftheregion.The
freshwaterthesepondsprovideisamajorfactorinthe
highsocio‐economicimportanceaffordedtopondsinthe
pIAPs.
OnlyonesitewasaffordedrecognitionbyitsdesignationasaUNESCOBiosphereReserve(Massifdu
Bouhachem).Theothersreceivenoprotectionatall,inspiteofthepresenceofprotectedspecies
andimportanthabitattypes.
ThreatstothepondresourceinNorthernAfricaaresignificantincludingextractionofmineralsfrom
thepondbasin,excessivegrazingpressure,pollution,eutrophication,mismanagementofwater
resources,climatechangeandacombinationofalloftheabove.
IAPcodeSitenameIAPSiteProfile
Pageno
21
MR01BabBerred216
MR02Benslimane219
MR03MassifduBouhachem222
MR04Casablanca225
MR05Chaouia 228
MR06Doukkala‐Abda231
MR07Essaouira 234
MR08Gharb237
MR09Haouz‐Jbilets240
MR10HautAtlas243
MR11Mamora246
MR12MoyenAtlas249
MR13AinEch‐Chair252
MR14OuedCherrat255
MR15PeninsuleTingitane258
22
WesternNumidia,Algeria
3.7 Algeria and Tunisia
Only4pIAPswereidentifiedinAlgeria.Allqualified
becauseofthedensityofponds,presenceof
protectedspecies,habitatsofhighconservation
importance,andsocio‐economicvalue.pIAPsranged
insizefrom70805ha(WesternNumidia)to300000
ha(Alger).Thedensityofpondsintheseareaswas
veryhighforthisbiogeographicregionandin
commonwithMorocco,localcommunities
dependedonthesepondsforfreshwater,industry
andagriculture.Twosites,EasternandWestern
Numidia,weredesignatedasRamsarsiteswhilstthe
othertwopIAPswereaffordednolegislative
protection.
InTunisiaanother4pIAPswereselected.Thesevariedwidelyinsize,from0.6ha(MajenCoucha)to
30000ha(Kroumirie).Thesitesqualifiedundereverycriterionincludingtheimportanceandrarityof
wetlandhabitatwithinthisregion(CriteriaE‐Other).TwositesaredesignatedasRamsarwetlands
(KroumirieandMajen
Chitane)whilstthe
othertwositesreceive
noprotection.Threats
tothesepondsrelateto
humanactivitiesandan
increaseintheduration
ofsummerdrought,
duetoclimatechange.
IAPcodeSitenameIAPSiteProfile
Pageno
AL01Alger261
AL02Jijel264
AL03WesternNumidie267
AL04EasternNumidie 270
TN01Kroumirie273
TN02MajenChoucha276
TN03MajenChitane279
TN04GaraaSejnane282
23
BrichatSecherpool,Israel
3.8 Middle East
IntheMiddleEast,asinglepIAPwasidentifiedineachof
Libya,Syria,Lebanon,EgyptandIsrael.Allqualifiedbecause
ofthepresenceofprotectedspecies,includingSecherin
Israelwhichispartofacomplexofpondsprovidingbreeding
habitatformetapopulationsofseveraldifferentamphibian
species.ThisIAPisaffordedsomeprotectionatanational
level.
Intheothercountriesallsitesqualifiedunderthefourmain
criteria:presenceofaprotectedspeciesandhabitat,pond
densityandsocio‐economicimportance.However,noneof
thesesitesreceivedanyprotection.Asaresulttheyarevery
vulnerabletohighlevelsofthreatfromhumanactivities.
IAPcodeSitenameIAPSiteProfile
Pageno
EG01Nile285
IS01BrichatSecherpool288
LB01Bekaa291
LYB01Cyrenaique294
SYR01Homs297
24
ZonesHumidesdesMenuires,FrancePlatzierJoch,Austria
4. THEALPINEARC
TheAlpsarethemostsignificantmountainrangeinEuropecoveringanareaof190000km2.They
formacrescentaround1,200kmlongand200kmwide,resultingfromthecollisionbetweenAfrica
andEurope.Largedifferencesinclimatefromnorthtosouthandwithaltitudecreateacontinuum
ofdifferenthabitattypes.Thesehabitatssupportarichdiversityofplant(13000)andanimal(30000)
speciesmanyofwhichareendemictothisregion.However,theAlpsarealsohometo14million
peopleandasignificantnumberoftouristsyearround.
TheAlpineArcincludespartsorallofGermany,Austria,France,Italy,thePrincipalityof
Liechtenstein,thePrincipalityofMonaco,SloveniaandSwitzerland.Thesecountriesaresignatories
totheprotocolagreedattheAlpineConvention(1991)whichaimedtocreatea“nationalandcross‐
bordernetworkofprotectedareas,biotopesandotherenvironmentalassetsprotectedor
acknowledgedasworthyofprotection”.
AsaresultofthisinitiativetheAlpsisnowlargelyprotectedbynationalparksandnaturereserves
(25%oftheAlpineregion).However,eventhislevelofprotectionhasnotsecuredthesurvivalof
manyimportantpondswhichremainoutsideofprotectedareas.Theprimarythreatisfrom
degradationduetohabitatfragmentationresultinginisolatedpopulationswhichcannotbe
sustainedinthelong‐termeveniftheyarewithinaprotectedarea.Thisisespeciallytrueintheface
ofclimatechangewhichhashadandwillcontinuetohavenegativeeffectsonthesehighaltitude
sites.Pondsandlakesinthisregionprovidevitalsteepingstonesacrossthelandscapeaswellas
beinganimportantbiodiversityresourceintheirownright.
FortheidentificationofIAPsfourcountrieswithintheAlpineArcwereselected,Switzerland,France,
AustriaandItaly,concentratingonlandover1500m.Atthisaltitudethreehabitatzonescanbe
identified,subalpine,alpineandnival,wherepondssupportmanyspeciesadaptedtolow
temperatureslivingwithinanarrowtemperaturerange(stenothermalspecies).
25
Atotalof30IAPshavebeenidentifiedintheAlpineArcregion(Figure3).Thesepondclusterswere
identifiedusingbothGISremotesensingtechniquesandbiologicaldata,particularlythepresenceof
Odonataandamphibians.IntheAlpineregion,themainthreattoproposedIAPsislinkedtohigh
levelsoftouristactivity.Inadditionclimatechangeisasignificantthreattospeciesadaptedtohigh
altitudeecosystems(Rossetetal.2010),whichwillrequirethinkingbeyondprotectedsite
boundaries.
Figure3:OverviewofthelocationofpIAPsintheAlpineArcRegion.
AUSTRIA
ITALY
SWITZERLAND
FRANCE
26
DormillousePonds,France
4.1 France
IntheFrenchregionoftheAlpineArc,8
pIAPshavebeenidentified.Mostarelocated
withintheSavoiedistrict,intheRhône‐Alps
region.ThesepIAPsqualifiedbecauseofthe
presenceofpriorityspecies,orbecauseof
thepresenceofimportantassemblagesof
stenothermaldragonflies.DormillousePonds
alsoqualifiedbecauseofthepresenceof
priorityhabitats.Somesiteshadhighpond
densities,between10and50pondsperkm2,
whilstotherswereonlyformedof1pond.
Sizesrangedfrom16ha(LacdesSaisies)to
over1000ha(ZonesHumidesdesMenuires).
SitesalsoqualifiedasIAPsonthebasisof
theirsocio‐economicimportance,whichincluded
grazingandtourism.However,thesetwofactorsalso
representsignificantthreatstotheponds.TheseIAPs
receivedsomelevelofprotectionas“Zonesnaturelle
d'intérêtécologique,faunistiqueetfloristique”and5
werewithinNatura2000sites.However,thethreatof
climatechange,asignificantthreattothesehigh
altitudeecosystems,willneedtobeaddressedbeyond
thesedesignatedareas.
IAPcodeSitenameIAPSiteProfile
Pageno
FR01LacdesSaisies300
FR02ZoneshumidesdeslacsdelaTempêteetducol
delaLouze302
FR03ZoneshumidesdesMenuires304
FR04ZoneshumidesducoldesEncombres306
FR05LacsdegorgesduDorondeTermignon308
FR06ZoneshumidesdeslacsPotron310
FR07LacsduplateauduTaillefer312
FR08EtangsdeDormillouse314
27
Grimselpass,Totesee,Switzerland
4.2 Switzerland
IntheSwissregionoftheAlpineArc,14pIAPshavebeenidentified.Thetypesofpondrepresented
werealluvialwetlands,postglacialmargins,glacialcirques,orhighaltitudebogsandmarshes.This
regionisnotableinhavingallpIAPslocatedabove2000m,withtheexceptionofGolfSamedan
(1700m);onesite(LaisdaMacun)wasabove2650m.Asaresultthesesitessupportcold
stenothermalspecialists(includingOdonata),whichareatparticularriskofclimatechange.
TheSwisspIAPsiteswereidentifiedunderthecriteriaofponddensity,whichvariedbetween10‐30
pondsperkm2.ThehighestponddensitywasrecordedatGlacierdeTsanfleuron,Steiseeam
SustenpassandGrimselpass(Totesee).ThepIAPsinthisregionvariedinsurfaceareafrom81ha
(Rinderstock,Plattisee)to360ha(LaisdaMacun).Somesitesqualifiedbecauseofthepresenceof
protectedamphibians,butformanybiologicaldatawerenotavailable.