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A preliminary assessment of Important Areas for Ponds (IAPs) in the Mediterranean Basin and Alpine Arc

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The Important Areas for Ponds (IAPs) concept was developed to raise awareness of geographic regions that support ponds of national or international biodiversity importance, and help focus strategies for pond monitoring, protection and appropriate management and creation. Ponds are vitally important for freshwater biodiversity and particularly recognised as stepping stone habitats. They also provide a range of ecosystem services and have been used for centuries by local communities. Ponds and pond networks are abundant across Europe and Northern Africa, in spite of significant losses, but are not adequately protected by current legislation even within the European legislative framework for nature conservation and water management. The information gathered during the identification of IAPS will be used to encourage better protection measures for ponds at the regional, national and international level, and their inclusion in biodiversity and water protection strategies (e.g. Water Framework Directive, River Basin Management Plans). In order to achieve greater protection for ponds in Europe there needs to be coordination between countries. The European Pond Conservation Network (EPCN), as part of the ProPond Project (Promoting Pond Conservation in Europe and the Mediterranean Region, a project supported by the MAVA foundation), has begun this work by concentrating on two biogeographical regions – the Mediterranean Basin and the Alpine Arc. Selection of IAPs was based on a set of criteria including the presence of species or habitats of conservation importance, pond density, and their socio‐economic importance (providing this did not undermine their biodiversity value) and other factors such as important assemblages of species e.g. dragonflies and macrocrustaceans. IAPs were identified using both GIS techniques and expert knowledge from a wide range of pond workers including both researchers and practitioners. For this first analysis, 140 proposed IAPs (pIAPs) have been identified in the Alpine Arc (30 pIAPs) and in the Mediterranean region (110 pIAPs), the latter including sites both from Northern Africa and the Middle East (28 pIAPs) and from Europe (82 pIAPs). A profile of each IAP has been produced with information on its (i) location, (ii) biodiversity, historical and social value, and (iii) threats. In the Mediterranean basin, pIAPs have been identified in 17 countries in Southern Europe, North Africa and the Eastern Mediterranean. The selected pIAPs reflect the heterogeneity of pond sites, and range from individual ponds in Spain supporting 18 species of European conservation importance to pond networks in Italy known to contain over 60 species of European conservation importance. Many areas qualified as IAPs because of high pond density (e.g. over 15 ponds per km2 in Greece) whereas others qualified because they contained many ponds scattered over large areas (e.g. 1613 ponds over 200000 ha in Morocco), representing a dispersed but highly significant freshwater biodiversity resource in the region. The socio‐economic value of ponds was also recognised in their identification as pIAPs: some such as in Israel show evidence of continuous use since the Roman occupation.Many IAPs, particularly in Northern Africa and the Eastern Mediterranean have no current protection, in spite of the habitats and species of conservation concern they support, and all are under significant threat from the increasing pressures of agriculture and development. Raising the profile of these sites through designation as IAPs will help to secure their protection and future sustainable management In the Alpine Arc, a total of 30 pIAPs were proposed in the four main countries which made up the region. Some had exceptionally high pond densities (e.g. pIAPs with over 30 ponds per km2 in the French Alps), whereas others in the same region comprise a single pond with important assemblages of species. Pond networks were also identified: some extended over large areas, exceeding 2000 ha in Italy, whilst others (e.g. in Austria) were concentrated within an area of less than 20ha. The majority of pIAPs in the Alpine Arc contained species of European conservation importance but also high altitude stenothermal species. However, these alpine ponds are not well represented in the list of pond types given under the Habitats Directive leading to a lack of designation within the European legislative framework of protected sites. The identification of networks of ponds in the Alpine region as IAPs will provide greater recognition of their importance to biodiversity at an international level. This is particularly relevant to high altitude sites, as they are under significant threat from climate change, an issue which requires cooperation and implementation of conservation initiatives at an international level. IAPs in the Alpine Arc also demonstrate the cultural importance of ponds. Many have a long history of use particularly within the traditional pastoral economy of the region. More recently pond networks are providing a valuable research and educational tool for both the scientific community and the wider public. This report is a preliminary assessment of IAPs in the Mediterranean and Alpine Arc region. Proposed IAPs (pIAPs) will be reviewed through a public consultation process and either accepted as a full IAP, modified or declined. The pIAPs identified as part of the ProPond Project will be published on the EPCN website. This should ensure that the information is rapidly disseminated to pond conservation practitioners and turned into positive action to protect and enhance the pond biodiversity resource. The pIAPs presented in this report incorporate the high quality ponds so far known: we anticipate that, as the profile and knowledge of ponds grows, aided by the IAP process itself, considerably more high quality pond will be found in these regions than have currently identified. The EPCN will now continue to coordinate and facilitate this work, building on the momentum of the ProPond project. A key role of the network and its members is now to disseminate the information presented here as widely as possible as part of a consultation process, but also to inform international and national policymakers.
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Apreliminaryassessmentof
ImportantAreasforPonds(IAPs)
inthe
MediterraneanBasinandAlpineArc
TechnicalReport
GarganoandTremitiIslands,ItalyLacsdesGorgesduDorondeTermingnon
©DrGuiseppeAlfonso France
 ©http://www.destinationtermignon.com
CONSULTATIONDOCUMENT
Preparedforthe
EuropeanPondConservationNetwork(EPCN)
by
NaomiEwald1,PascaleNicolet12,BeatOertli3ValentinaDellaBella2,LailaRhazi4,AnneSophie
Reymond3,EliseMinssieux3,ErriyahiSaber5,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
5CEGAUMR«ESPACE»andUniversityofProvence,AixMarseilleI,France
6DepartmentofBiology,FacultyofSciencesandTechniquesofErrachidia,MouslayIsmailUniversity,
BP509Boutalamine,Errachidia,Morocco
Thisreportshouldbecitedas:
EwaldN,NicoletP,OertliB,DellaBellaV,RhaziL,ReymondAS,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),hasbegunthisworkbyconcentratingontwobiogeographicalregionsthe
MediterraneanBasinandtheAlpineArc.
SelectionofIAPswasbasedonasetofcriteriaincludingthepresenceofspeciesorhabitatsof
conservationimportance,ponddensity,andtheirsocioeconomicimportance(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.Thesocioeconomicvalueofpondswasalso
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,vascularandlowerplantsandmicroorganisms,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.Pondsaregenerallytoosmalltofitthestandardmodelofsitebasedprotectionandthey
donotfitthestandardmodelofconsentbasedprotectiondesignedtoprotectwaterbodieslike
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
arenotedinArticle10assteppingstonehabitats,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
extensionofNatura2000sitestononEUcountries,althoughitisnotlegallybinding.The
concentrationofMediterraneanTemporaryPonds,asdefinedbyNatura2000,withinNorthern
AfricashouldqualifymanysitesidentifiedaspartoftheIAPprocessforinclusionintheEmerald
Network.Severalotherinternationaldesignationsmayalsoaffordpondsitessomeprotection,
althoughdesignationstendtobenonlegallybinding,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
nongovernmentalorganisations),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.).
Ithasbeenshownthatpondswithhighsocioeconomicvalueareoftenmanagedmoresustainably
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
metapopulationsofpondassociatedplantsandanimals
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
particularsocioeconomicimportance.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
ofpIAPlocationsandacrossreferencetothepagenumbersofeachpIAPsiteprofileinthe
accompanyingdocument.
8
3. THEMEDITERRANEANBASIN
TheMediterraneanregionisdefinedbyitsclimate.Duringthesummeritreceivessubtropicaldry
andwarmair,whilstinthewintertheregionexperiencescyclonicmaritimestormsfromthePolar
Regions.Thisisoftendescribedasawinterrain,summerdryclimate.
Therigoursoflivinginthistypeofextremeclimatehaveresultedinahighdegreeofendemismin
thearea.Thisisreflectedinthenumberofpriorityspecies(Natura2000)recordedhere(59%ofall
priorityspeciesonAnnexII).Theclimatealsopromotestheformationoftemporaryponds.In
NorthernAfricathesearethepredominantpondtype,supportingauniqueanddiverseplantand
animalcommunity.Temporaryponds,however,donotconstituteahomogeneousgroupandvary
considerablydependingonlocalphysicochemicalcharacteristicssuchassoilsandsurfacearea.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
ongoinginthesepIAPstomaintainandenhancethepondresource.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
SP14LebrijaLasCabezasponds 33
SP15LosArenalesponds 35
SP16MalladasdelaDevesa 37
SP17Menorca39
SP18RedondaorMelchorGomezpond 43
SP19SantaOlallaPonds45
SP20CompejoLagunarCarsticodeCuenca 47
SP21HoyadeBezas49
SP22Trujillanapond51
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*),includingsiteswhicharebothmanmade
(RoqueHaute)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
FR04CentreVar86
FR05Costieres88
FR06Crau90
FR07Biot93
FR08MaredeCatcheou95
FR09Massifd'Esterel98
FR10PlainedesMauresandMassifdesMaures101
FR11Camargue104
FR12Pezenas107
FR13Rodes109
FR14RoqueHaute111
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
MAL01SanPawltatTargapools 191
18
SchiniasMarathonPonds,Greece
3.5 Balkan States and Cyprus
IntheEasternMediterranean,7pIAPswere
identifiedinGreeceandCyprus.Thesesites
qualifiedbecauseofthepresenceofprotected
speciesandhabitats,andallwerewithinthe
Natura2000network,withtheexceptionof
KamposKarystoupIAP.ThesepIAPswere
predominantlyinlowlyingareaswhichputsthem
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
highsocioeconomicimportanceaffordedtopondsinthe
pIAPs.
OnlyonesitewasaffordedrecognitionbyitsdesignationasaUNESCOBiosphereReserve(Massifdu
Bouhachem).Theothersreceivenoprotectionatall,inspiteofthepresenceofprotectedspecies
andimportanthabitattypes.
ThreatstothepondresourceinNorthernAfricaaresignificantincludingextractionofmineralsfrom
thepondbasin,excessivegrazingpressure,pollution,eutrophication,mismanagementofwater
resources,climatechangeandacombinationofalloftheabove.
IAPcodeSitenameIAPSiteProfile
Pageno
21
MR01BabBerred216
MR02Benslimane219
MR03MassifduBouhachem222
MR04Casablanca225
MR05Chaouia 228
MR06DoukkalaAbda231
MR07Essaouira 234
MR08Gharb237
MR09HaouzJbilets240
MR10HautAtlas243
MR11Mamora246
MR12MoyenAtlas249
MR13AinEchChair252
MR14OuedCherrat255
MR15PeninsuleTingitane258
22
WesternNumidia,Algeria
3.7 Algeria and Tunisia
Only4pIAPswereidentifiedinAlgeria.Allqualified
becauseofthedensityofponds,presenceof
protectedspecies,habitatsofhighconservation
importance,andsocioeconomicvalue.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
densityandsocioeconomicimportance.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
sustainedinthelongtermeveniftheyarewithinaprotectedarea.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,intheRhôneAlps
region.ThesepIAPsqualifiedbecauseofthe
presenceofpriorityspecies,orbecauseof
thepresenceofimportantassemblagesof
stenothermaldragonflies.DormillousePonds
alsoqualifiedbecauseofthepresenceof
priorityhabitats.Somesiteshadhighpond
densities,between10and50pondsperkm2,
whilstotherswereonlyformedof1pond.
Sizesrangedfrom16ha(LacdesSaisies)to
over1000ha(ZonesHumidesdesMenuires).
SitesalsoqualifiedasIAPsonthebasisof
theirsocioeconomicimportance,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,whichvariedbetween1030
pondsperkm2.ThehighestponddensitywasrecordedatGlacierdeTsanfleuron,Steiseeam
SustenpassandGrimselpass(Totesee).ThepIAPsinthisregionvariedinsurfaceareafrom81ha
(Rinderstock,Plattisee)to360ha(LaisdaMacun).Somesitesqualifiedbecauseofthepresenceof
protectedamphibians,butformanybiologicaldatawerenotavailable.