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Assessment of golden jackal species (Canis aureus, L.1758) records in natural areas out of their known historic range

Authors:

Abstract

Golden jackals show an increasing long-distance dispersal from their known historic geographic range into new areas (Rutkowski et al. 2015). Only in the last years, single golden jackal individuals were reported in Latvia, Lithuania, Poland, Germany or Denmark and a survival cluster of 5 territorial groups (Männil 2016, pers. comm.) is monitored in West Estonia. The known historic range of the golden jackal species including large parts of Eurasia and Africa was recently reconsidered since the results of new genetic studies suggest that African golden jackals merit recognition as a full species - they meet the primary defining criterion of a separate and independently evolving metapopulation lineage (Rueness et al. 2011; Gaubert et al. 2012; Koepfli et al. 2015). Accordingly, it was proposed that the common names ‘‘African golden wolf’’ (Canis anthus) and ‘‘Eurasian golden jackal’’ (Canis aureus) be applied to distinguish these taxa and to distinguish the former from the Ethiopian wolf (Canis simensis). The African golden wolf is distributed across Africa and includes individuals that have been referred to as Canis lupus lupaster or Canis aureus, sensu lato. Morphologic parallelism of African golden wolves and Eurasian golden jackals may have resulted in their mistaken attribution to a single species (Koepfli et al. 2015). Over the past two decades evidences northward and westward of the known historic range, mostly the Balkan area, were recorded (Kryštufek et al. 1997; Arnold et al. 2011). The native and naturally colonized range of golden jackals in Europe now include Greece, Albania, Montenegro, Republic of Macedonia, Bosnia-Herzegovina, Serbia, Bulgaria, Romania, Hungary, Croatia, Slovenia, Switzerland, Italy, Austria, Slovakia, Czech Republic, Moldova, Ukraine, Turkey, Caucasus countries, Belarus, Estonia, Latvia, Lithuania, Poland, Germany and Denmark. Central and South-East Europe have now a very important role in the golden jackal species conservation since the European or Caucasian golden jackal (Canis aureus moreoticus, I. Geoffroy Saint-Hilaire, 1835) is known as having its main populations in Bulgaria, Greece, Serbia, Croatia, Hungary and Romania. The main problem in assessing golden jackal proof in new areas is inexperience due to the novelty and rareness of these situations to this point. This report aims to establish common criteria within European countries and abroad for golden jackal species new records that are reported in areas within naturally colonized range.
Assessment of golden jackal species (Canis aureus
, L.1758) records in  
naturalareasoutoftheirknownhistoricrange
TechnicalReport:GOJAGECriteriaandGuidelines
12ofFebruary2016GOJAGEeBulletin
JenniferHATLAUF,OvidiuC.BANEA,LucaLAPINI
2016©GOJAGEGoldenJackalInformalStudyGroupEurope
1)Introduction
Golden jackals show an increasing longdistance dispersal from their known historic
geographic range into new areas (Rutkowski et al. 2015). Only in the last years, single  
golden jackal individuals were reported in Latvia, Lithuania, Poland, Germany or Denmark
and a survival cluster of 5 territorial groups (Männil 2016, pers. comm.
) is monitored in       
WestEstonia.
The known historic range of the golden jackal species including large parts of Eurasia and
Africa was recently reconsidered since the results of new genetic studies suggest that
African golden jackals merit recognition as a full species  they meet the primary defining  
criterion of a separate and independently evolving metapopulation lineage (Rueness et al
.  
2011;Gaubert et al. 2012;Koepfli et al. 2015). Accordingly, it was proposed that the  
common names ‘‘African golden wolf’’ (Canis anthus
) and ‘‘Eurasian golden jackal’’ (Canis     
aureus
) be applied to distinguish these taxa and to distinguish the former from the
Ethiopian wolf (Canis simensis
). The African golden wolf is distributed across Africa and    
includes individuals that have been referred to as Canis lupus lupaster or Canis aureus
,       
sensu lato. Morphologic parallelism of African golden wolves and Eurasian golden jackals
mayhaveresultedintheirmistakenattributiontoasinglespecies(Koepflietal.
2015).
Over the past two decades evidences northward and westward of the known historic
range, mostly the Balkan area, were recorded (Kryštufek et al. 1997; Arnold et al. 2011).  
The native and naturally colonized range of golden jackals in Europe now include Greece,
Albania, Montenegro, Republic of Macedonia, BosniaHerzegovina, Serbia, Bulgaria,
Romania, Hungary, Croatia, Slovenia, Switzerland, Italy, Austria, Slovakia, Czech
Republic, Moldova, Ukraine, Turkey, Caucasus countries, Belarus, Estonia, Latvia,
Lithuania, Poland, Germany and Denmark. Central and SouthEast Europe have now a
very important role in the golden jackal species conservation since the European or
Caucasian golden jackal (Canis aureus moreoticus
, I. Geoffroy SaintHilaire, 1835) is    
known as having its main populations in Bulgaria, Greece, Serbia, Croatia, Hungary and
Romania.
The main problem in assessing golden jackal proof in new areas is inexperience due to
the novelty and rareness of these situations to this point. This report aims to establish
common criteria within European countries and abroad for golden jackal species new
recordsthatarereportedinareaswithinnaturallycolonizedrange.
2)Methods
These methods are used by members of the GOlden JAckal informal study Group in
Europe (GOJAGE). More than 80 scientists from Europe and abroad form this group. Its
sole purpose is to gather information about the golden jackal population ecology and
biogeography in all European countries as well as the entire known range, and further to
communicatejointresearchactivitiesandspecializedspeciesintegratedmonitoring.
1
Directmethods
Indirectmethods
1) Livespecimen:directobservations
duringdaytimeorwithspotlight
2) Deadspecimen:roadkilled,
harvestedorconserved
3) Laboratory
 Identification by sampling saliva that is left
in connection to bite wounds on prey or
scavengedremnants,otherspecimentissues
Hair,urineordroppingsnuclearDNA
1) BioAcousticStimulation(BAS)
2) Photoandvideotrapping
3) Fieldwork:searchingfordens,tracks
andsignsduringsurveystages,
ecologicalfactorsassessment
4) Questionnaires,Interviews
5) Huntingbagdata,availablelocal
newspaperandliteraturereview
3)Criteria
To avoid misleading estimations of the golden jackal range or species misidentification we
suggest the classification of new reports into three categories based on the reliability of the
evidence adopted and modified from SCALP (Status and Conservation of the Alpine Lynx    
Population) of MolinariJobin et al. (2003). We added a new category to clearly  
discriminate reliability of evidence (C1,C2,C3 categories) from no evidence: this category
is C4 (No Evidence). We also proposed additional criteria (GOJAGE Expert Criteria) based
on complementary expert analysis using GOJAGE direct and indirect methods like direct
observations, genetic analysis of liquids, excrements and hair, BAS, photo and video
trapping, questionnaires, hunting, not verified reports presented in local newspapers,
fieldwork or specific surveys. This process will permit a better assessment of the golden
jackalspeciesrangeexpansion.
Category
Nr&Name
GOJAGEExpert/NonExpertCriteria
modifiedfromSCALP
GOJAGEExpertCriteria
number of methods with positive results
assessedalwaysbyexperts
C1
Strong
Evidence
Unchallenged observations from experts
“hard facts” e.g. all reports of golden jackals
killed or found dead and photographs taken
byexperts
 threeindirectmethods
OR
 onedirectmethod
C2
Verified
Evidence
Sightings,recordsoftracksanddroppings
→ifreportedorverifiedbyexperts
 threeindirectmethods
C3
Weak
Evidence
Sightings,recordsoftracksanddroppings
→ reported by nonexperts as well as all      
sightings and spontaneous howls that cannot
beverified
 twoindirectmethods
C4
No
Evidence
Sightings,recordsoftracksanddroppings
→ reported by nonexperts as well as all      
sightings and spontaneous howls that cannot
beverified
 nomethod
2
Forassessingareportyoucanfollowthekeyprotocol„Distinctionofgoldenjackal
evidence“
attheendofthistechnicalreport:GOJAGEGUIDELINES
Reports of C2, C3 categories could change into a C1 category if new mentioned methods
are performed by experts and after new analysis with GOJAGE Expert criteria. If reports
cannot be assessed according to these recommendations or to the GOJAGE guidelines,
theserecordsshouldbeignoredandclassifiedasC4(NoEvidence).
4)Whattodowithpotentialevidence?
If a supposed golden jackal specimen is seen, photographed or found dead, the following
stepsaresuggested.
4.1Report
→ Shot or roadkilled: Take a photo of the specimen (whole animal/ breast/ paws/ tail)    
and report it to the Nature Protection Authorities and the GOJAGE team. If this is not
possible a sample of muscle tissue (for example from inner hind leg muscle) for genetic
analysiscanbetaken.
→Photograph:SendthePicturetotheGOJAGEexpertteam
→Track:Ifpossible,takeapicturewithareferenceobject(ortakeagypsumimpression)
→ Sighting: Write a note as detailed as possible (exact location, time, number of    
animals,...)totheGOJAGEexpertteam
4.2Verification
The habitat should additionally be verified  Pictures or videos (also photo and video
camera trappings) etc. can support the report. Species experts should investigate
ecologicalfactorsinordertocompletethefindings.
4.3FieldworkwiththeGOJAGEexpertteam
The GOJAGE team will perform bioacoustic monitoring (BAM) or census, habitat
assessment and species ecology assessment with or without costs according to local
nature protection or game management authorities. For bioacoustic monitoring it is
suggestedtoassigncategoriestojackalhowlingsignaturesaswell:
BAMC1
Strongevidence(typicalyiphowlsequences)
BAMC2
Equivocalordoubt(onlyoneanimal,barkingorwithoutyiphowl)
BAMNR
Anotherspeciesornoresponse,thissituationrequiresfurtherstudies
5)Legalframework(AnnexVaandVIfromtheEUHabitatsDirective)
The golden jackal (Canis aureus
) is a Community Interest species ("Habitats Directive"       
92/43/EEC) listed in Annex Va together with pine marten (Martes martes
), European  
polecat (Mustela putorius
) and chamois (Rupicapra rupicapra
). Monitoring of conservation    
status is an obligation arising from Article 11 of the Habitats Directive for all habitats (as
listedinAnnexI)andspecies(aslistedinAnnexII,IVandV)ofCommunityinterest.
Consequently, this provision is not restricted to Natura 2000 sites and data need to be
collected both in and outside the Natura 2000 network to achieve a full appreciation of the
3
conservation status. The main results of this monitoring need to be reported to the
Commission every six years according to Article 17 of the directive. Article 14 places a
requirement for further surveillance of exploited species of flora and fauna listed in Annex
V where necessary. Only after monitoring and scientific reports to the Commission,
managementmeasurescanbeassessed.
When management measures are applied in case of Community Interest species like   
the golden jackal or chamois a series of hunting methods should be avoided. These
hunting methods which are prohibited are listed in the Annex VI of the "Habitats      
Directive"92/43/EEC.
6)RepresentativesofGOldenJAckalinformalstudyGroupEuropeGOJAGE
Country
Name
Contact
Romania
OvidiuC.Banea
ovidiubanea@gmail.com
Romania
CristianR.Papp
papp_cr@yahoo.co.uk
Italy
LucaLapini
lucalapini@libero.it
France
NathanRanc
nathan.ranc@gmail.com
Spain
DanielPerezVazquez
danipeva@yahoo.es
Portugal
FranciscoAlvares
falvares@cibio.up.pt
Austria
JenniferHatlauf
hatlauf@hotmail.com
Greece
GiorgosGiannatos
ygiannatos@gmail.com
Greece
DespinaMigli
desmigli@gmail.com
Hungary
LászlóSzabó
mag.polaris@gmail.com
Hungary
MiklósGáborHeltai
heltai.miklos@gmail.com
Hungary
JózsefLanszki
lanszkij@gmail.com
Slovenia
MihaKrofel
miha.krofel@gmail.com
Bulgaria
NikolaiSpassov
nspassov@nmnhs.com
Bulgaria
IlyaAcostaPankov
ilyaacosta@gmail.com
Bulgaria
StoyanStoyanov
stoyans@abv.bg
Serbia
DuškoĆirović
dcirovic@bio.bg.ac.rs
Serbia
AleksandraPenezić
aleksandra.penezic@yahoo.com
Croatia
IvanaSelanec
ivanaselanec@gmail.com
CzechRepublic
JaroslavČervinka
jara.cervinka@centrum.cz
CzechRepublic
MartinŠalek
martin.sali@post.cz
Poland
WieslawBogdanowicz
wieslawb@miiz.waw.pl
Lithuania
GintarėŽalkauskaite
gintare.zalkauskaite@gmail.com
Estonia
PeepMännil
peep.mannil@gmail.com
Germany
FelixBöcker
fel.boecker@googlemail.com
Ukraine
MykolaRozhenko
rogenkonikolaj@gmail.com
Ukraine
AndriyTarasBashta
atbashta@gmail.com
Ukraine
GrigoriyKolomytsev
g.kolomytsev@gmail.com
Ukraine
VasylPrydatko
vasylprydatko@yahoo.com
Ukraine
IgorZagorodniuk
zoozag@ukr.net
Turkey
CoşkunTez
tezc@erciyes.edu.tr
Turkey
OsmanIbis
ibis.osman@gmail.com
Belarus
ValeryDombrovski
valdombr@rambler.ru
GOJAGE members (2011): Giorgos Giannatos (Greece), Luca Lapini (Italy), Dumitru Murariu  
(Romania), Miha Krofel (Slovenia), Dusko Cirovic (Serbia), László Szabó (Hungary), Ovidiu Banea        
(Romania), Petre Gargarea (Romania), Daniel Perez Vazquez (Spain), Jaroslav Cervinka (Czech
Republic), Martin Salek (Czech Republic), Aleksandra Penezic (Serbia), Frank Zachos (Austria),
Mark Hajdu (Hungary), Letizia Kozlan (Italy). GOJAGE members (20122016): Ivana Selanec    
(Croatia), Alexandra Grigore (Romania), Nicoleta Dinculescu (Romania), Krassimir Kurtev    
4
(Bulgaria), Gabriella Dragne (Greece), Dan Vasiu (Romania), Franco Milani (Italy), Stefano
Pecorella (Italy), Tomaž Berce (Slovenia), CristianRemus Papp (Romania), Coşkun Tez (Turkey),
Osman Ibiş (Turkey), Mateja Deržič (Slovenia), Jasna Mladenovič (Slovenia), Ivan Budinski
(Croatia), Lejla Colic (Croatia), Stefano Filacorda (Italy), Andrea Caboni (Italy), Luca Dorigo (Italy),
Marco Pavanello (Italy), Peep Männil (Estonia), Kaja Lotman (Estonia), Liisi Laos (Estonia), Alex
Lotman (Estonia), Tonis Ulm (Estonia), Antti Halkka (Finland), Hiroshi Tsunoda (Japan), Ilya
Acosta Pankov (Bulgaria), Felix Böcker (Germany), Dominique Van Asperen (Greece), Igor
Zagorodniuk (Ukraine), Mykola Rozhenko (Ukraine), Sergey Zhyla (Ukraine), Valery Dombrovski
(Belarus), Viktor Demianchik (Belarus), Elena Dyatlova (Ukraine), AndriyTaras Bashta (Ukraine),
Jose Luis Alvarez Piernas (Spain), Lucian Parfon (Romania), Radu Mot (Romania), Chandika
Jayaratne (Sri Lanka), Maria Petridou (Greece), Grygoriy Kolomytsev (Ukraine), Michelle Drew
(Australia), Stoyan Stoyanov (Bulgaria), Timo Maran (Estonia), Janez Tarman (Slovenia), Julie K.
Young (USA), Jeffrey Sweetbaum (Montenegro), Nathan Ranc (France), Wojciech Solarz (Poland),
Sebastijan Lamut (Slovenia), Anita Kurys (Hungary), Francisco Jorge Álvares (Portugal), Maciej
Romanski (Poland), Gintarė Žalkauskaite (Lithuania), Jos Stratford (United Kingdom), Aakriti Singh
(India), Jennifer Hatlauf (Austria), Klaus Hackländer (Austria), Janos Botond Kiss (Romania),
Liselotte Wesley Andersen (Denmark), Neculai Selaru (Romania), Calin Gherman (Romania),
Vladimir Talpes (Romania), Angela Ionica (Romania). Scientific support: Janosch Arnold      
(Austria), Boris Krystufek (Slovenia), Grigore Baboianu (Romania), Nikolai Spassov (Bulgaria),
VassilGolemansky(Bulgaria),WieslawBogdanowicz(Poland),VasylPrydatko(Ukraine).
Literature
Arnold Janosch, Humer Anna, Heltai Miklós, Murariu Dumitru, Spassov Nikolai, and Hackländer Klaus. 2011.
“Current Status and Distribution of Golden Jackals Canis Aureus in Europe.” Mammal Review 42 (1):
1–11.
Gaubert, Philippe, Cécile Bloch, Slim Benyacoub, Adnan Abdelhamid, Paolo Pagani, Chabi Adéyèmi Marc
Sylvestre Djagoun, Arnaud Couloux, and Sylvain Dufour. 2012. “Reviving the African Wolf Canis Lupus
Lupaster in North and West Africa: A Mitochondrial Lineage Ranging More than 6,000 Km Wide.” PloS
One7(8):e42740.
Koepfli, KlausPeter, John Pollinger, Raquel Godinho, Jacqueline Robinson, Amanda Lea, Sarah Hendricks,
Rena M. Schweizer, et al. 2015. “GenomeWide Evidence Reveals That African and Eurasian Golden
JackalsAreDistinctSpecies.”CurrentBiology:CB25(16):2158–65.
Kryštufek B., Murariu D., and Kurtonur C. 1997. “Present Distribution of the Golden Jackal Canis Aureus in the
BalkansandAdjacentRegions.”MammalReview27(2):109–14.
MolinariJobin, A., Molinari, P., BreitenmoserWürsten, C., Wölfl, M., Stanisa, C., Fasel, M., Stahl, P., Vandel,
J., Rotelli, L., Kaczensky, P., Huber, T., Adamic, M., Koren, I., & Breitenmoser, U. (2003). PanAlpine
ConservationStrategyfortheLynx.Natureandenvironment130,CouncilofEuropePublishing.
Rueness, Eli Knispel, Maria Gulbrandsen Asmyhr, Claudio SilleroZubiri, David W. Macdonald, Afework Bekele,
Anagaw Atickem, and Nils Chr Stenseth. 2011. “The Cryptic African Wolf: Canis Aureus Lupaster Is
NotaGoldenJackalandIsNotEndemictoEgypt.”PloSOne6(1):e16385.
Rutkowski, Robert, Miha Krofel, Giorgos Giannatos, Duško Ćirović, Peep Männil, Anatoliy M. Volokh, József
Lanszki, et al. 2015. “A European Concern? Genetic Structure and Expansion of Golden Jackals
(CanisAureus)inEuropeandtheCaucasus.”PloSOne10(11):e0141236.
5
Distinctionofgoldenjackal(Canisaureus,
L.1758)evidencesGOJAGEGUIDELINES
WHO
REPORTS
EXPERTINVITED
KEY
QUALITY
GOJAGE
CRITERIA
Expert
Positive
Sure
C1
Doubt
Possible
C3
Non‐Expert
yes
Positive
Sure
C1
Doubt
Possible
C3
Negative
Wrong
C4
No
Possible
C3
Laboratory
Positive
Sure
C1
Negative
Wrong
C4
Withoutlaboratory
‐butwithexpert
Positive
Possible
C2
Doubt
Unsure
C3
Negative
Wrong
C4
Withoutlaboratory
Unsure
C3
Expert
Positive
Sure
C2
Doubt
Possible
C3
Negative
Wrong
C4
Non‐Expert
Yes
Positive
Sure
C2
Doubt
Possible
C3
Negative
Wrong
C4
No
Unsure
C3
Expert
Positive
Likely
C2
Doubt
Possible
C3
Negative
Wrong
C4
Non‐Expert
Yes**
Positive
Possible
C3
Doubt
Unsure
C3
Negative
Wrong
C4
No
Unsure
C3
Expert
Positive
(yip‐howl)
Sure
BAMC1
Doubt
(1animal,
barking)
Possible
BAMC2
Negative
Wrong***
BAMNR***
Non‐Expert
Yes**
Positive
Unsure
C3
Doubt
Unsure
C3
Negative
Wrong
C4
No
Unsure
C3
6
*Iftheseevidencesarenotavailableanymore,whencontrolled–assessmentoftheevidenceshouldbedealtwithaccordingto
„sightings“
**Evaluationofplausibility
***BAMNRsituationrequiresfurtherinvestigationsasfornow,noresponsedoesnotexcludespeciespresence
Qualitydescriptions:
This table is adapted from the criteria proposal for lynx monitoring from the Forstliche Versuchs und Forschungsanstalt      
BadenWürtemberg (www.wildtiermonitoring.de) that includes SCALP Criteria (MolinariJobin et al. 2003). Their criteria enable an   
evenmoredistinctassessmentthroughadditionalQualitydescriptions:1.sure2.likely3.possible4.unsure5.wrong
GOJAGEDATABASE
Newgoldenjackalreportsdatabasewillbeupdatedandperiodicallypublishedintheonline
GOJAGEeBulletin(here)
ToreportnewrecordsyoucancontactGOJAGErepresentativesormembersinyourowncountry(chapter6).
Toreportrecordsoutofknownrangepleasecontact:
Mrs.JenniferHatlauf,MSc
inWildlifeEcologyandWildlifeManagement,GOJAGE
Email:hatlauf@hotmail.com
PleaseprovidedataasisshowedinthefollowingtableandwaitGOJAGEexpertise
CATEGORY
thiscolumnis
reservedto
GOJAGEexpert
DATE
AGE
ifavailable
GENDER
ifavailable
LOCATION
‐City,country
‐GPScoordinates
EXPERT
NON‐EXPERT
‐name,contactdetails
Correspondingauthors:GOJAGECo‐Founders
OvidiuC.Banea,EnvironmentalEcologist,MSc.
EcologyDept.ofCrispusNGOSibiu,
Str.Muncel5/79550320SIBIU,ROMANIA.
Phone:0034‐661557293
LucaLapini,Biologist,Dr.inNat.Sciences
ZoologicalSect.oftheFriulianNaturalHistoryMuseum,
ViaMarangoni39,I33100UDINE,ITALY.
Phone:0039‐3461576021
7
... The standards are mainly based on the monitoring standards for lynx, wolves and bears (Molinari-Jobin et al., 2003, Reinhardt et al., 2015. Several ideas from the first proposals for practicable criteria specifically for golden jackals from Hatlauf et al. (2016) were expanded and practical experiences of the consulted experts were integrated. ...
... The original name for the categorisation "SCALP" (Status and Conservation of the Alpine Lynx Population), introduced by Molinari-Jobin et al., (2012), was retained. In 2016, participants of the Golden Jackal Informal Study Group in Europe (GOJAGE) drafted standards for monitoring the golden jackal in Europe (Hatlauf et al., 2016), which, however, are not applied consistently across Europe and we have therefore supplemented these within this text. The standardised assessment of golden jackal records is also intended to enable the large-scale creation of occurrence maps, based on the SCALP criteria for lynx, wolf and bear. ...
Book
Full-text available
The golden jackal is colonizing new habitats where it did not exist before. This creates a new situation in many areas, which poses a new challenge for recording and monitoring. The European legal situation and the increasing social and political interest make a structured and comparable monitoring of the golden jackal more and more necessary. Today, established monitoring standards of wolf, lynx and bear allow the comparison of collected data in many European countries. Only common monitoring rules and forms of presentation make it possible to provide reliable and comprehensible data across political borders. In order to meet these requirements for the further monitoring of the golden jackal occurrence in Central Europe we developed recommendations for the monitoring of the golden jackal. The aim was to create a monitoring basis for Central European and other bordering countries to ensure transparency and comparability in golden jackal monitoring.
... Throughout their range, the population of the golden jackal declined until the 1960s due to habitat fragmentation, culling practices and intensive hunting persecutions. During the 1980's, number of golden jackals increased in the core area and from the end of the century the dispersion of the species increased towards the North and West of Europe (Kryštufek & Tvrtković 1990, Krofel & Potočnik 2008, Lapini et al. 2009, Arnold et al. 2012, Trouwborst et al. 2015, Hatlauf et al. 2016, Ranc 2016. Some studies suggested that natural causes and anthropogenic influences as well as the presence of other top predators, especially stablished wolf packs, can influence their patterns of fast dispersion and establishment in new territories (Giannatos et al. 2005, Šálek et al. 2014, Newsome et al. 2015, Trouwborst et al. 2015, Krofel et al. 2017. ...
... Literature research targeted scientific articles, non-published literature, websites from hunting groups, publications in hunting magazines and relevant personal communications. Classification of collected evidence was done based on the assessment criteria from SCALP (Breitenmoser et al. 2006), adapted by GOJAGE (Hatlauf et al. 2016). Within this review, shot and found dead individuals were classified as C1 and registered observations as C3. ...
Article
Full-text available
The golden jackal (Canis aureus Linnaeus, 1758) is one of the most widespread canid species. Nowadays, it is a permanent species from the Slovak fauna. In recent years, their number has grown and the dispersion range has increased in our country. The first evidence of this species was recorded in 1947 and after 1989 the records of jackal presence increased steadily, most originating from the South of Slovakia. The presence of the golden jackal was quite evident from 2009 until 2016 as results demonstrate a great significance in terms of numbers during this period. The collected data is very consistent between culling data (strong evidence) and opportunistic observations (presumable evidence). Patterns of first migrating individuals presented in this work, confirmed previsions of the direction of the dispersion of this species to North from the Balkans region. Presumably, much of the migration occurred from Hungary as most of the first official records of the golden jackal in Slovakia are from areas close to the Hungarian border. This work aims to review and evaluate available official data and literature of Canis aureus in Slovakia. It also intends to summarise the status of this species and correlate it with historical data.
... Both video recordings from different locations realized on 12 and 31 of March were accepted by the group members as belonging to the species of golden jackal. On the basis of GOJAGE guidelines criteria, expert criteria and expert/non-expert criteria (Hatlauf et al , 2016), those records could be classified now as strong evidence (C1). The question of a survival population cluster in NE Denmark raised the group´s interest and one member arrived to Lille Vildmose protected areas and performed bio-acoustic stimulation from 6 calling stations together with both photographers from Olympus Danmark on 1st of April 2017. ...
... The results of BAM are non-conclusive and incomplete (Figure 1). According to GOJAGE Guidelines (Hatlauf et al 2016) when BAM is NR (another species answers or there is no response), this situation requires further studies. ...
Technical Report
Full-text available
The golden jackal records in Denmark were updated in the beginning of April 2017 with the last species sighting on 31 of March 2017 by two photographers from Olympus Denmark, Troels Kjær and Henrik Friis. The question of a survival population cluster in NE Denmark raised the group´s interest and one member arrived to Lille Vildmose protected areas and performed bio-acoustic stimulation from 6 calling stations together with both photographers from Olympus Danmark on 1st of April 2017. Henrik Friis and Troels Kjær recorded the second alive specimen in Lille Vildmose the day before while they were checking their photo-cameras. The first sighting in the region was reported in summer 2016 by Carsten Clausen. The last recorded specimen probably is a female, due to urine marking behavior analysis from the recorded videos. To assume that a survival jackal species population cluster exists in the region there is a need of documenting jackal evidence for over two consecutive years in the area. Furthermore, the demonstration of reproduction or territorial behavior is required. The golden jackal was recorded two times in NE Jutland in the same area of Lille Vildmose Natural Park in less than a year. We suggest that wolves may represent a vector for the jackal distribution but this was not demonstrated for Denmark yet. Against this theory it is known that jackals live with wolves mostly in a parapatric pattern (Krofel et al, 2017). The ecological factors which determine the golden jackal persistence in NE Jutland are not known. BAM cannot be used to assess vagrant individuals and needs to be continued with a frequency not higher than one survey every 3-6 months. To this monitoring technique, additional methods like, fieldwork looking for footprints, droppings, camera trap or scent detection dog can be admitted to complete the holistic monitoring approach before any management actions. The establishment of reproductive golden jackal groups in NE Denmark will also depend on human intervention and anthropogenic support of the species.
... Results of new genetic studies suggest that the African golden jackals (Canis anthus, F. Cuvier 1820) should merit recognition as a full, separate species (Rueness et al. 2011;Gaubert et al. 2012;Koepfli et al. 2015). Therefore, Central and South-East Europe hold an important role in the golden jackal species conservation and management, as the main populations of the European jackal, also called Caucasian jackal (Canis aureus moreoticus, I. GeoffroySaint-Hilaire, 1835) are especially known to be in Bulgaria, Greece, Serbia, Croatia, Hungary and Romania (Hatlauf et al., 2016a;Arnold et al., 2012;Kryštufek et al., 1997). Thus, in new colonisation areas, far outside known historical range like in regions of the Baltic countries, Poland, Germany, Denmark or the Netherlands the golden jackal is one of the least known mammals. ...
... To minimise bias as far as possible and utilize standardised assessment of golden jackal answers, the following categories were assigned for this survey (Hatlauf et al. 2016a): 1) The typical high-pitched " yip-howls " from golden jackals are rated as strong evidence – BAM (BioAcoustic Monitoring) C1, because of its distinctiveness to other species. 2) It may also occur that single individuals respond to the playback; for example 38 % in a study in Croatia (Krofel, 2008) and 43 % single jackals in areas in Italy (Comazzi et al., 2016). ...
... Based on an initial citizens reports (Supplementary material), 26 jackal-howling emission sessions were performed northeast of Parma (about 109km 2 area) during January, November and December 2021, and January, February, July, August and September 2022. Bio-acoustic methods have been applied using the standard GOJAGE stimulus and procedure (Hatlauf et al. 2016). ...
Article
Although the presence of the golden jackal (Canis aureus moreoticus) in Italy has been documented since 1984, it has long been considered an accidental species confined to a limited portion of the northeastern sector of the country. Recently, dispersing individuals of golden jackal have been reported in different areas of northern Italy, suggesting an enhanced spreading attitude compared to the past. However, despite a wider covered area, no evidence of reproductive groups south of the Po River has ever been documented, suggesting possible geographical limitations due to the habitat or ecological conditions. This study witnesses the overcoming of this large freshwater course by the species, and describes the first reproductive group of golden jackals south of Po River in a context of a highly industrialized area. The results are obtained using different methods (citizen science, howling, camera trapping, search of signs) able to demonstrate an expansion of this mesocarnivore outside its traditional northeastern Italian distribution range. Interesting questions are also raised about the species ecology with special regard to its southern migration pattern through anthropic zones.
... Bei Bedarf sollen diese Standards bei regelmäßigen internationalen Treffen weiterentwickelt und angepasst werden. Bei der Ausarbeitung der Standards wird sich vor allem an den Monitoringstandards für Bär, Luchs und Wolf orientiert (Molinari-Jobin et al. 2003, Reinhardt et al. 2015, Ideen der ersten Vorschläge für praktikable Kriterien speziell für Goldschakale wurden erweitert (Hatlauf et al. 2016) und praktische Erfahrungen der konsultierten Experten integriert. ...
Article
Full-text available
https://boku.ac.at/fileadmin/data/H03000/H83000/H83200/Publikationen/BOKU-Berichte/BOKU_Berichte_zur_Wildtierforschung_26.pdf Das Monitoring von Großen Beutegreifern in Europa hat in den vergangenen Jahren an Bedeutung gewonnen und wurde mit viel Expertise weiterentwickelt. Der Hintergrund hierfür ist die Ausbreitung von Luchs, Wolfund Bärin vielen Ländern und Gegenden. Neben diesen Tierarten gewinnt auch der Goldschakal immer weiter an Bedeutung. Die Tierart breitet sich in Gebieten Osteuropas wieder aus, in denen die Art bis in die 50er Jahre stark zurückgedrängt wurde. Aber auch in Regionen, in denen der Goldschakal nie heimisch war,wie in Zentral-West-und Nordeuropawerden zunehmend Nachweise registriert. Große Entfernungen zu bekannten Vorkommensgebietenund eine neue Situation in Regionen, in denen die Tierart erstmals auftaucht,machen einen internationalen Austausch zwischen europäischen Ländern empfehlenswert. Somit wächst auch das Bestreben bei der Nachweiserhebung und -bestätigung nach einheitlichen Standards vorzugehen, wie dies bei Luchs,Wolfund Bärbereits vielerorts der Fall ist.Im Folgenden werden Vorschläge für ein einheitliches Vorgehen und eine einheitliche Beurteilung von Hinweisen im Monitoring des Goldschakals in Abstimmung mit Fachpersonen aus Deutschland, Österreich und der Schweiz beschrieben.Bei Bedarf sollen diese Standards bei regelmäßigen internationalen Treffen weiterentwickelt und angepasst werden. Bei der Ausarbeitung der Standards wird sich vor allem an den Monitoringstandards für Bär, Luchs und Wolf orientiert (Molinari-Jobin et al.2003, Reinhardt et al.2015), Ideen der ersten Vorschläge für praktikable Kriterien speziell für Goldschakale wurden erweitert (Hatlauf et al.2016) und praktische Erfahrungen der konsultierten Experten integriert.
... Scats and footprints with intermediate characteristics between similar species (i.e. the golden jackal and the red fox) were discarded; regarding the scats, we discarded those of 13-14 cm due to the overlap in their size with those of the red fox (total length range: 3-14 cm). Howls were recorded only if the typical yip howl sequences were heard (Hatlauf et al. 2016). Every sign of presence was autonomously evaluated by the researchers conducting the fieldwork and discordant records were discarded. ...
Article
Full-text available
Compared with the rapid expansion across Europe, the golden jackal colonization of Italy is still limited and slow. No study focused on the habitat selection or landscape connectivity for this species was performed in Italy; thus, the potential distribution and dispersal patterns in the country remain unknown. Our objectives were to evaluate the suitability of the Friuli-Venezia Giulia region (north-eastern Italy) for the golden jackal, as well as to identify the ecological corridors connecting the areas currently occupied by the species. Corridors modelling allowed us both to hypothesize the dispersal dynamics occurring in the study region and to identify possible obstacles to future range expansion. We surveyed golden jackal presence in two study areas, covering an area of 500 km 2 , from March 2017 to February 2018. Using collected data, we modelled the species home-range scale habitat suitability based on an ensemble modelling approach. Subsequently, a habitat suitability prediction at a finer scale was used to estimate landscape resistance, starting from which, we modelled dispersal corridors among areas currently occupied by the species using a factorial least cost path and a cumulative resistant kernel approach. Our results indicated a moderate potential for large parts of the study region to support the occurrence of golden jackal family groups, whose presence seems to be mainly driven by the presence of wide areas covered by broadleaved forests and shrublands and by the absence of wide intensive agricultural areas. The predicted connectivity networks showed that three main permeable corridors are likely to connect golden jackal occurrence areas within the study region, while all the other corridors are characterized by a very low path density. Both the habitat selection and connectivity analyses showed a strong negative impact of the intensive cultivated plain on species stable presence and movement providing critical information for the conservation of the golden jackal in Italy.
Article
Full-text available
Introduction The European large carnivore community is recently showing positive trends. Beyond those, other species are expanding in Europe. In recent decades, the golden jackal (Canis aureus), a medium-sized canid, has rapidly expanded to western and northern Europe, after being historically confined to the Balkans. The Eurasian lynx (Lynx lynx), an apex predator once widely distributed throughout Europe, was nearly eradicated in the 19th century. Recent reintroductions, legal protection, and its natural expansion brought the lynx to recover, though some populations still face extinction. As the carnivores’ community across Europe is rearranging, ecological interactions are changing as well. Indeed, recent observations reported the golden jackal to kleptoparasitize the lynx. Our research aims to predict the potentially suitable habitats for the golden jackal and the Eurasian lynx, detailing the areas where those are expected to coexist soon. Methods We model their distribution in Europe for current and future scenarios, using both citizen-science and literature data, using the latter to buffer the possible biases of the former. For this aim, we included not only climatic variables, but also several biotic and abiotic predictors relevant to both species. Moreover, given his strong influence on the golden jackal, we compare our results with the predicted distribution of the grey wolf (Canis lupus). Results Our predictions show an increase in habitat suitability for the golden jackal, while an opposite trend is predicted for the Eurasian lynx. Also, we predict the target species to share a large portion of their range in the future, with most of these areas suitable for wolves, too. Discussion Our results may have several impacts in the context of large-scale management, helping to predict further expansion of the golden jackal, and to identify critical areas for lynx conservation, supporting the management of possible reintroductions, also shedding light on the large carnivores’ changing community
Article
Full-text available
Conflicts have emerged due to range expansions of the golden jackal (Canis aureus) across Europe, characterized by their international conservation status and perceived impacts on livestock and native prey species. Most countries in Central Europe do not yet include the golden jackal in their national list of occurring, native species. Nevertheless, legal obligations arise as soon as golden jackals colonize a particular country. Legal implications of this range expansion were described in past studies from an international perspective. However, they left out specifics on the legal status within any particular country. Therefore, we examine the actual legal status within Central European countries, exemplifying the diverse federal and provincial laws. In particular, we assess the current conservation and hunting laws in Austria’s provinces and discuss them in the context of neighbouring countries to analyse implications for relevant authorities. We found substantial contrasts not only among provinces but also between direct neighbouring countries, impeding efforts for transboundary species conservation and leading to complications regarding the management of this species. Improved procedures for collecting records and hunting-bag data appear necessary for future species assessment on a European level and management on a local level. We recommend a more unified legal system but adjusted to actual golden jackal presence on the regional and cross-border level, combined assessment, or similar management strategies to minimize conflicts, reduce persecution, and clarify legal obligations.
Thesis
Full-text available
The golden jackal (Canis aureus LINNAEUS, 1758) is probably the most exemplary representation of all dog-like carnivores. Originally indigenous to Western Asia and Eastern Europe, it now settles in large parts of Asia, Africa and Europe. Since the end of the 20th century, the opportunistic predator spreaded increasingly in Central Europe. Coming from Bulgaria, Hungary, Romania, Serbia and Croatia the golden jackal population has expanded into Western and Northern Europe. Evidence of this natural distribution have been discovered as far north as Estonia and Denmark; and as far west as Switzerland and the Netherlands. The migratory behaviour of the golden jackal is dictated by physical geography, enabled through corridors between impassable rivers and other barriers such as mountain ranges. Difficulty in observing this hidden living mammal mandates for further scientific research and international standardisations for data collection to appreciate its expansion realistically. For the monitoring of established packs, the bio-acoustic method is implementable. In general, the combination of several methods appears to be efficient. An overview of the present state of the golden jackal in Europe is provided by a recent distribution map. Allowing for statements about future movements of the golden jackal, which is likely to expand over the whole of Europe. Today this canid is probably more widespread than presently assumed.
Article
Full-text available
In the first continent-wide study of the golden jackal (Canis aureus), we characterised its population genetic structure and attempted to identify the origin of European populations. This provided a unique insight into genetic characteristics of a native carnivore population with rapid large-scale expansion. We analysed 15 microsatellite markers and a 406 base-pair fragment of the mitochondrial control region. Bayesian-based and principal components methods were applied to evaluate whether the geographical grouping of samples corresponded with genetic groups. Our analysis revealed low levels of genetic diversity, reflecting the unique history of the golden jackal among Europe's native carnivores. The results suggest ongoing gene flow between southeastern Europe and the Caucasus, with both contributing to the Baltic population, which appeared only recently. The population from the Peloponnese Peninsula in southern Greece forms a common genetic cluster with samples from southeastern Europe (ΔK approach in STRUCTURE, Principal Components Analysis [PCA]), although the results based on BAPS and the estimated likelihood in STRUCTURE indicate that Peloponnesian jackals may represent a distinct population. Moreover, analyses of population structure also suggest either genetic distinctiveness of the island population from Samos near the coast of Asia Minor (BAPS, most STRUCTURE, PCA), or possibly its connection with the Caucasus population (one analysis in STRUCTURE). We speculate from our results that ancient Mediterranean jackal populations have persisted to the present day, and have merged with jackals colonising from Asia. These data also suggest that new populations of the golden jackal may be founded by long-distance dispersal, and thus should not be treated as an invasive alien species, i.e. an organism that is “non-native to an ecosystem, and which may cause economic or environmental harm or adversely affect human health”. These insights into the genetic structure and ancestry of Baltic jackals have important implications for management and conservation of jackals in Europe. The golden jackal is listed as an Annex V species in the EU Habitats Directive and as such, considering also the results presented here, should be legally protected in all EU member states.
Article
Full-text available
The golden jackal Canis aureus is one of the most widespread canid species with a range covering areas of central, eastern and southern Europe, northern Africa and parts of Asia. Distribution of the golden jackal in Europe has been dynamic, including dramatic declines (until the 1960s), recovery (1960s and 1970s) and expansion (from the early 1980s onwards). We present up‐to‐date information on golden jackal status in Europe and range expansion. For data collection we reviewed the scientific literature and contacted scientists from the relevant countries. We distinguished between vagrant animals and established populations. In the last decade, there has been an increase in jackal records in areas where the species has not been reported before. Increased presence is recorded northwards and westwards of the distribution range of the golden jackal, specifically in Hungary, Serbia and Slovakia. In Austria, the first case of reproduction was confirmed in 2007; reproduction has also recently been reported in Italy. Results indicate an ongoing expansion in Europe's jackal population, with a particular spread of the Balkan populations towards central Europe. Although there are numerous reports of sightings, only few originate from confirmed sources and in many areas status is unknown or vague. There is a general lack of ecological data and almost no information on ecological consequences associated with the golden jackal expansion.
Article
Full-text available
The recent discovery of a lineage of gray wolf in North-East Africa suggests the presence of a cryptic canid on the continent, the African wolf Canis lupus lupaster. We analyzed the mtDNA diversity (cytochrome b and control region) of a series of African Canis including wolf-like animals from North and West Africa. Our objectives were to assess the actual range of C. l. lupaster, to further estimate the genetic characteristics and demographic history of its lineage, and to question its taxonomic delineation from the golden jackal C. aureus, with which it has been considered synonymous. We confirmed the existence of four distinct lineages within the gray wolf, including C. lupus/familiaris (Holarctic wolves and dogs), C. l. pallipes, C. l. chanco and C. l. lupaster. Taxonomic assignment procedures identified wolf-like individuals from Algeria, Mali and Senegal, as belonging to C. l. lupaster, expanding its known distribution c. 6,000 km to the west. We estimated that the African wolf lineage (i) had the highest level of genetic diversity within C. lupus, (ii) coalesced during the Late Pleistocene, contemporaneously with Holarctic wolves and dogs, and (iii) had an effective population size of c. 80,000 females. Our results suggest that the African wolf is a relatively ancient gray wolf lineage with a fairly large, past effective population size, as also suggested by the Pleistocene fossil record. Unique field observations in Senegal allowed us to provide a morphological and behavioral diagnosis of the African wolf that clearly distinguished it from the sympatric golden jackal. However, the detection of C. l. lupaster mtDNA haplotypes in C. aureus from Senegal brings the delineation between the African wolf and the golden jackal into question. In terms of conservation, it appears urgent to further characterize the status of the African wolf with regard to the African golden jackal.
Article
Full-text available
The Egyptian jackal (Canis aureus lupaster) has hitherto been considered a large, rare subspecies of the golden jackal (C. aureus). It has maintained its taxonomical status to date, despite studies demonstrating morphological similarities to the grey wolf (C. lupus). We have analyzed 2055 bp of mitochondrial DNA from C. a. lupaster and investigated the similarity to C. aureus and C. lupus. Through phylogenetic comparison with all wild wolf-like canids (based on 726 bp of the Cytochrome b gene) we conclusively (100% bootstrap support) place the Egyptian jackal within the grey wolf species complex, together with the Holarctic wolf, the Indian wolf and the Himalayan wolf. Like the two latter taxa, C. a. lupaster seems to represent an ancient wolf lineage which most likely colonized Africa prior to the northern hemisphere radiation. We thus refer to C. a. lupaster as the African wolf. Furthermore, we have detected C. a. lupaster individuals at two localities in the Ethiopian highlands, extending the distribution by at least 2,500 km southeast. The only grey wolf species to inhabit the African continent is a cryptic species for which the conservation status urgently needs assessment.
Article
The golden jackal of Africa (Canis aureus) has long been considered a conspecific of jackals distributed throughout Eurasia, with the nearest source populations in the Middle East. However, two recent reports found that mitochondrial haplotypes of some African golden jackals aligned more closely to gray wolves (Canis lupus) [1, 2], which is surprising given the absence of gray wolves in Africa and the phenotypic divergence between the two species. Moreover, these results imply the existence of a previously unrecognized phylogenetically distinct species despite a long history of taxonomic work on African canids. To test the distinct-species hypothesis and understand the evolutionary history that would account for this puzzling result, we analyzed extensive genomic data including mitochondrial genome sequences, sequences from 20 autosomal loci (17 introns and 3 exon segments), microsatellite loci, X- and Y-linked zinc-finger protein gene (ZFX and ZFY) sequences, and whole-genome nuclear sequences in African and Eurasian golden jackals and gray wolves. Our results provide consistent and robust evidence that populations of golden jackals from Africa and Eurasia represent distinct monophyletic lineages separated for more than one million years, sufficient to merit formal recognition as different species: C. anthus (African golden wolf) and C. aureus (Eurasian golden jackal). Using morphologic data, we demonstrate a striking morphologic similarity between East African and Eurasian golden jackals, suggesting parallelism, which may have misled taxonomists and likely reflects uniquely intense interspecific competition in the East African carnivore guild. Our study shows how ecology can confound taxonomy if interspecific competition constrains size diversification. Copyright © 2015 Elsevier Ltd. All rights reserved.
Article
Small, scattered, but resident, populations of Golden Jackal Canis aureus occur along the coasts of the Balkan Peninsula. The bulk of these European Jackals is concentrated in the eastern parts of the Peninsula, mainly in Bulgaria. The northern border of the resident population lies along the Danube in the Walachian Plain of Romania, and in Srem (Yugoslavia). Vagrants may appear far outside the Balkans in north-eastern Italy, Slovenia, Austria, Hungary and Slovakia. Whilst the species is in decline in Greece, it has expanded its area in Bulgaria from = 2400 km2 in 1962 to 80 000 km2 in 1985, i.e. a 33-fold range increase within 23 years.
Angela Ionica (Romania) ​ Scientific support: Janosch Arnold (Austria) Boris Krystufek (Slovenia
  • Vladimir Talpes
Vladimir Talpes (Romania), Angela Ionica (Romania). ​ Scientific support: Janosch Arnold (Austria), Boris Krystufek (Slovenia), Grigore Baboianu (Romania), Nikolai Spassov (Bulgaria), Vassil Golemansky (Bulgaria), Wieslaw Bogdanowicz (Poland), Vasyl Prydatko (Ukraine).