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In the Baltic countries, the golden jackal (Canis aureus) was first recorded in Estonia on 28 February 2013 and three specimens of golden jackal were hunted in Latvia in 2014. The first golden jackal in Lithuania was hunted on 7 February 2015. The species of the golden jackal was identified using morphological and mitochondrial DNA control region (CR1) analysis. In Lithuania, hunting of these animals is permitted throughout the year. Few studies in the past revealed the potential role of the golden jackal as a carrier of intestinal helminths, parasites, and zoonotic diseases. In this study, the presence of tick-borne pathogens and other parasites in golden jackal specimen were investigated. No pathogens (Anaplasma phagocytophilum, Babesia sp., Bartonella sp.) were found in the spleen of the golden jackal. However, the flukes Apophallus donicus, nematodes Uncinaria stenocephala, and unidentified individuals of class Cestoda were detected. Helminths A. donicus and U. stenocephala are not new species for Lithuania and neighbouring territories.
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BIOLOGIJA. 2018. Vol. 64. No. 3. P. 203–207
© Lietuvos mokslų akademija, 2018
e golden jackal Canis aureus–anew
species in theBaltic countries
*Corresponding author. Email: algimantas.paulauskas@vdu.lt
AlgimantasPaulauskas1*,
IrmaRažanskė1,
JanaRadzijevskaja1,
DovilėNugaraitė1,
VaclovasGedminas2
1Vytautas Magnus University,
VileikosSt.8, Kaunas 44404,
Lithuania
2Kaunas Tadas Ivanauskas
Zoological Museum,
LaisvėsAv. 106, Kaunas 44253,
Lithuania
In theBaltic countries, thegolden jackal (Canis aureus) was rst
recorded in Estonia on 28February2013 and three specimens
of golden jackal were hunted in Latvia in 2014. erst golden
jackal in Lithuania was hunted on 7February2015. especies
of thegolden jackal was identied using morphological and mi-
tochondrial DNA control region (CR1) analysis. In Lithuania,
hunting of these animals is permitted throughout theyear. Few
studies in thepast revealed thepotential role of thegolden jackal
as acarrier of intestinal helminths, parasites, and zoonotic diseas-
es. In this study, thepresence of tick-borne pathogens and other
parasites in golden jackal specimen were investigated. No patho-
gens (Anaplasma phagocytophilum, Babesia sp., Bartonella sp.)
were found in thespleen of thegolden jackal. However, theukes
Apophallus donicus, nematodes Uncinaria stenocephala, and uni-
dentied individuals of class Cestoda were detected. Helminths
A.donicus and U. stenocephala are not new species for Lithuania
and neighbouring territories.
Keywords: Canis aureus, mtDNA, helminths, Uncinaria steno-
cephala, Apophallus donicus, Cestoda
INTRODUCTION
e golden jackal (Canis aureus) is a native
Palearctic species with ahistoric range extending
from North Africa and South-eastern and Central
Europe through to Central and East Asia (Jhala
and Moehlman, 2008). epopulation and dis-
tribution of thegolden jackal within Europe has
seen considerable changes over recent decades.
Since themid-twentieth century, thedistribution-
al range of golden jackals has expanded signi-
cantly across Central and Eastern Europe with oc-
casional animals being documented to thenorth
and thewest, far from theestablished populations
in theareas and countries they had not been re-
corded before. Golden jackals have been recent-
ly sighted as far west as Switzerland and as far
north as Estonia (Rutkowskiet al., 2015; Trouw-
borstetal., 2015).
In Estonia and Latvia, golden jackals of un-
known origin have been recorded since 2011 (Ba-
nea, 2013; Toom, 2014; Trouwborstet al., 2015).
erst conrmed case of thegolden jackal in
the Baltic countries was reported in Estonia in
2013. In February 2013, agolden jackal was killed
by hunters in Matsalu National Park, West Estonia
(Männiletal., 2014). In 2014, golden jackals were
recorded in several other widely dispersed locali-
ties across Estonia, including thenorth, north-
east and south of thecountry. Until May 2015,
204 Algimantas Paulauskas, Irma Ražanskė, Jana Radzijevskaja, Dovilė Nugaraitė, Vaclovas Gedminas
a total of nine individuals were killed either
by hunters or in road accidents across Estonia
(Stratford, 2015).
First recorded cases of thegolden jackal in
Latvia were three individuals killed by ahunter
in July and December 2013 (Männiletal., 2014).
Until 2015, atotal of ten golden jackals were shot
or found dead in Latvia (Stratford, 2015).
In Lithuania, therst golden jackal was shot
in February 2015. especies of the hunted
individual was identied through a morpho-
logical examination. Since that time, other un-
conrmed reports of thegolden jackal followed
from thedistricts of Kaunas, Vilnius, Zarasai,
Varėna, and Biržai.
In thepresent study, we used mitochondrial
DNA control region data for theconrmation
of species identication, and as few studies in
thepast revealed thepotential role of thejack-
als as carriers of zoonotic diseases, we investi-
gated thepresence of tick-borne pathogens and
other parasites in thegolden jackal specimen
from Lithuania.
MATERIALS AND METHODS
Genomic DNA from thespecimen spleen was ex-
tracted using theGenomic DNA Purication Kit
(ermo Fisher Scientic, Lithuania) according
to manufacturer’s instructions. DNA was stored
at –20°C until subsequent handlings. A460bp of
hypervariable le domain of themitochondrial
DNA control region was amplied using PCR
and sequencing primers WDLOOPL 5’-TCC-
CTGACACCCCTACATTC-3’, H519 5’-CGTT-
GCGGTCATAGGTGAG-3’ (designed on wolf
mtDNA CR (Canigliaetal., 2013)) as described
in Fabbrietal., 2014. eproducts were separat-
ed on 1.5% agarose gel and visualized by etidium
bromide. PCR amplication product of mtDNR
control region was puried using GeneJET Gel
Extraction Kit (ermo Fisher Scientic, Lithu-
ania) and sequenced. eresulting 460-bp-long
sequence of theCR mtDNA was revised manu-
ally and aligned with golden jackal sequences
from GenBank in MEGA6. esequence of CR
mtDNA was submitted to GenBank and assigned
thefollowing accession number: KT123040.
Conventional PCR and nested PCR methods
were used for thedetection of Anaplasma phago-
cytophilum, Babesiaspp., Bartonellaspp. (Mas-
sungetal., 1998; Raretal., 2005; Normanetal.,
1995).
Prior to helminthological investigation the
material was frozen at –80°C for 10 days for safe-
ty reasons (i.e., to avoid possible infection with
Echinococcusspp.) (WHO/OIE Manual, 2001).
egolden jackal was thawed at room tempera-
ture and separate organs (entire gastrointestinal
tract, lungs, heart, liver, and kidney) were stud-
ied helminthologically according to themethod-
ology of Ivashkinetal. (1971). Examination of
the content of the intestines and of the stomach
was based on the method of consistent ushing.
Helminths were picked out and xed in 70% eth-
anol for later examination. For themicroscopic
study, trematodes and nematodes were mounted
in glycerin and examined under aMotic BA400
Tension microscope. Identication was based on
thekey of Kozlov (1977). ediet of thegolden
jackal was studied using analysis of thestomach
content. Each portion of thestomach content
was mixed with water and individual compo-
nents separated into groups.
RESULTS AND DISCUSSION
Comparison of themtDNA sequence identied
in this study with those deposited in GenBank
conrmed that theanimal hunted in Lithuania
in February 2015 was agolden jackal (accession
number KT123040). egolden jackal haplotype
identied in thepresent study corresponds with
thehaplotype previously identied in Italy, Cro-
atia, Bulgaria, Serbia, and theCaucasus (Fig.1).
egolden jackal is anew species in theBaltic
region. econrmed cases of thegolden jack-
al in Latvia and Estonia were recorded in 2013
(Männiletal., 2014; Stratford, 2015), two years
earlier than in Lithuania.
e Eurasian golden jackal has been reported
as ahost of pathogens of zoonotic and veterinary
importance, including arange of vector-borne
pathogens such as Ehrlichia canis, Anaplasma
phagocytophilum, and others (Waneretal., 1999),
and only one Babesia species (B.canis) was
205
e golden jackal Canis aureus – a new species in the Baltic countries
conrmed by molecular methods in golden jack-
als in Europe, in Romania (Mitkovaetal., 2017).
However, reports of tick-borne pathogens in
C.aureus are scarce. In this study, dierent PCR
methods were used for the detection of tick-
borne pathogens: Anaplasma phagocytophilum,
Babesiaspp., Bartonellaspp. eresults of PCR
analysis were negative for all tested pathogens.
Several hookworm (Ancylostomatidae) spe-
cies have been reported in golden jackals, with
Ancylostoma caninum and Uncinaria stenoceph-
ala commonly reported across the entire geo-
graphical range of these hosts (Gherman, Mihal-
ca, 2017). In thesmall intestine of theLithuanian
golden jackal, 49 ukes of species Apophallus
donicus, 11 nematodes of species Uncinaria
stenocephala (Fig. 2), and 29 unidentied indi-
viduals of Cestoda were found.
e diet of golden jackal was studied through
thestomach content. It was found to consist of
Fig. 1. Phylogenetic tree of mtDNA sequences created using theNeighbor-Joining
method and abootstrap analysis of 1000 replicates. esample from thepresent
study is marked. Nyctereutes procyonoides are used as an out-group. Abbreva-
tions: BG–Bulgaria, HR–Croatia, IT–Italy, RS–Serbia
Fig. 2. Uncinaria stenocephala, microscopic
examination
206 Algimantas Paulauskas, Irma Ražanskė, Jana Radzijevskaja, Dovilė Nugaraitė, Vaclovas Gedminas
plants, insects (larvae), birds (feathers), rodents
(bones, limbs), and ungulates (hair). In Croatia,
both animal and plant components were found
in thescat of thegolden jackal: themajor com-
ponent was mammals (50.3%), followed by fruit
seeds and vegetables (34.1%), insects (29.5%),
birds (including eggs; 24.8%), articial materi-
als (24%), and branches, leaves, and grass (24%)
(Radovic, Kovačic, 2010).
CONCLUSIONS
Result of analysis of asample of unknown ani-
mal from Lithuania revealed that it was agold-
en jackal. Similar genetic patterns based on
mtDNA control region sequences were iden-
tied in animals from Bulgaria, Croatia, Italy,
Serbia, and theCaucasus. No tick-borne patho-
gens were found in thegolden jackal, however,
theukes Apophallus donicus, nematodes Unci-
naria stenocephala, and unidentied individu-
als of class Cestoda were detected.
ACKNOWLEDGEMENTS
e authors would like to thank thehunters for
thegolden jackal sample.
Received 8 October 2017
Accepted 12 April 2018
References
1. Banea O. Jackals in West Estonia. GOJAGE
blog: http://goldenjackalaround.blogspot. com/
2013/03/golden-jackal-survey-in-w-estonia.
html 1 March 2013. Accessed 3January 2018.
2. CanigliaR, FabbriE, MastrogiuseppeL, Ran-
diE. Who is who? Identication of livestock
predators using forensic genetic approaches.
Forensic Sci Int Genet. 2013; 7: 397–404.
3. Fabbri E, CanigliaR, Galov A, ArbanasicH,
Lapini L, Boskovic I, Florijancic T, Vlasse-
vaA, AhmedA, MirchevRL, RandiE. Gene-
tic structure and expansion of golden jackals
(Canis aureus) in thenorth-western distribu-
tion range (Croatia and eastern Italian Alps).
Conserv Genet. 2014; 15(1): 187–99.
4. GhermanCM, MihalcaAD. Asynoptic over-
view of golden jackal parasites reveals high
diversity of species. Parasit Vectors. 2017; 10:
419.
5. IvashkinVM, Sobolev AA, KhromovaL. Ca-
mallanata of animals and man and diseases
caused by them.) In: SkryabinKI, editor. Es-
sentials of nematodology. 1971; 22: 1–388.
Russian.
6. JhalaY, MoehlmanPD. Canis aureus. eIUCN
Red List of reatened Species. http://www.iuc-
nredlist.org/details/3744/0 (2008) [Cited 2018
Jan3].
7. KozlovMA. Anew genus and species of parasi-
toid of thefamily Platygastridae (Hymenoptera,
Proctotrupoidea) from Armenia. Trudy Zoo-
logicheskogo Instituta Akademii Nauk SSSR.
1977; 64: 79–81.
8. MännilP, JogisaluI, OzolinsJ, MaranT. Gold-
en jackal–new carnivore species in Northern
Europe? 9th Baltic eriological Conference,
Book of Abstracts, Daugavpils. 2014: 47.
9. MassungRF, SlaterK, OwensJH, Nichol-
sonWL, Mather TN, Solberg VB, OlsonJG.
Nested PCR assay for detection of granulocytic
Ehrlichiae. J Clin Microbiol. 1998; 36: 1090–5.
10. MitkováB, HrazdilováK, D’AmicoG, Dus-
cher GG, SuchentrunkF, ForejtekP, Gher-
manCM, MateiIA, IonicáAM, DaskalakiAA,
MihalcaD, VotýpkaJ, HulvaP, ModrýD. Eura-
sian golden jackal as host of canine vector-
borne protists. Parasit Vectors. 2017; 10: 183.
11. NormanAF, RegneryR, JamesonP, GreeneC,
KrauseDC. Dierentiation of Bartonella-like
isolates at thespecies level by PCR-restriction
fragment length polymorphism in thecitrate
synthase gene. J Clin Microbiol. 1995; 33(7):
1797–803.
12. RadovicA, KovačicD. Diet composition of the
golden jackal (Canis aureusL.) on thePelje{ac
Peninsula, Dalmatia, Croatia. Period Biol. 2010;
112(2): 219–24.
207
e golden jackal Canis aureus – a new species in the Baltic countries
13. RarVA, FomenkoNV, DobrotvorskyAK, Li-
vanovaNN, RudakovaSA, FedorovEG, Asta-
ninVB, MorozovaOV. Tickborne pathogen de-
tection, Western Siberia, Russia. Emerg Infect
Dis. 2005; 11(11): 1708–15.
14. RutkowskiR, KrofelM, GiannatosG, ĆirovićD,
MännilP, VolokhAM, etal. AEuropean con-
cern? Genetic structure and expansion of golden
jackals (Canis aureus) in Europe and theCauca-
sus. PLoS ONE. 2015; 10(11): e0141236.
15. StratfordJ. Golden jackal in Lithuania, acon-
sideration of its arrival, impact and status.
Zool Ecol. 2015; 25(4): 277–87.
16. TamuraK, StecherG, PetersonD, FilipskiA,
KumarS. MEGA6: Molecular evolutionary
genetics analysis version 6.0. Mol Biol Evol.
2013; 30: 2725–9.
17. TrouwborstA, KrofelM, LinnellJDC. Legal
implications of range expansions in a terres-
trial carnivore: the case of the golden jackal
(Canis aureus) in Europe. Biodivers Conserv.
2015; 24: 2593–610.
18. WanerT, BanethG, StrengerC, KeysaryA,
KingR, HarrusS. Antibodies reactive withEhr-
lichia canis,Ehrlichia phagocytophila genogroup
antigens and thespotted fever group rickettsial
antigens, in free-ranging jackals (Canis aureus
syriacus) from Israel. Vet Parasitol. 1999; 82:
121–8.
19. WHO/OIE (2001): Manual on Echinococco-
sis in Humans and Animals: a Public Health
Problem of Global Concern (ed. EckertJ, Gem-
mellMA, MeslinFX, PawlowskiZS). World
Organisation of Animal Health, Paris, France,
p.286, http://apps.who.int/iris/bitstream/10665
/42427/1/929044522X.pdf [Cited 2018Jan03].
AlgimantasPaulauskas, IrmaRažanskė,
Jana Radzijevskaja, DovilėNugaraitė,
VaclovasGedminas
PAPRASTASIS ŠAKALAS CANIS AUREUS
NAUJA RŪŠIS BALTIJOS ŠALYSE
Santrauka
Pirmą kartą paprastasis šakalas (Canis aureus)
Estijoje buvo pastebėtas 2013 m. vasario28d.,
Latvijoje pirmieji trys paprastieji šakalai buvo su-
medžioti 2014 metais. Lietuvoje pirmasis šakalas
sumedžiotas 2015m. vasario7d., šio gyvūno rūšies
identikacija atlikta remiantis morfologine ir mole-
kuline (mitochondrinės DNR) analize. Ankstesniais
tyrimais nustatyta, kad paprastieji šakalai gali būti
žarnyno helmintų ir zoonotinės kilmės ligų perne-
šėjai. Dabar buvo atlikti erkių pernešamų patogenų
ir žarnyno parazitų tyrimai. Erkių pernešamų pa-
togenų (Anaplasma phagocytophilum, Babesiasp.,
Bartonellasp.) paprastojo šakalo blužnies pavyzdyje
nerasta, žarnyne buvo aptiktos siurbikės (Apophallus
donicus), apvaliosios kirmėlės (Uncinaria steno-
cephala) ir neidentikuotos rūšies kaspinuočių
(Cestoda) klasės individai.
Raktažodžiai: Canis aureus, mitochondrinė
DNR, helmintai, Uncinaria stenocephala, Apophallus
donicus, kaspinuočiai
... The golden jackal has been recorded as far as in northern Norway (Sørensen & Lindsø 2021). The species was for the first time recorded in Estonia in 2011, in Latvia in 2013 and in Lithuania in 2015 (Paulauskas et al. 2018). The migrating individuals have already reached western Europe and the species appeared in Denmark in 2015 (Tillmann 2020), the first record doi: 10.37520/lynx.2023.012 in the Netherlands was made in 2016 (van der Grift 2016). ...
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The golden jackal (Canis aureus) is a species under significant and fast geographic expansion. Various parasites are known from golden jackals across their geographic range, and certain groups can be spread during their expansion, increasing the risk of cross-infection with other carnivores or even humans. The current list of the golden jackal parasites includes 194 species and was compiled on the basis of an extensive literature search published from historical times until April 2017, and is shown herein in synoptic tables followed by critical comments of the various findings. This large variety of parasites is related to the extensive geographic range, territorial mobility and a very unselective diet. The vast majority of these parasites are shared with domestic dogs or cats. The zoonotic potential is the most important aspect of species reported in the golden jackal, some of them, such as Echinococcus spp., hookworms, Toxocara spp., or Trichinella spp., having a great public health impact. Our review brings overwhelming evidence on the importance of Canis aureus as a wild reservoir of human and animal parasites.
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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.
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We announce the release of an advanced version of the Molecular Evolutionary Genetics Analysis (MEGA) software, which currently contains facilities for building sequence alignments, inferring phylogenetic histories, and conducting molecular evolutionary analysis. In version 6.0, MEGA now enables the inference of timetrees, as it implements our RelTime method for estimating divergence times for all branching points in a phylogeny. A new Timetree Wizard in MEGA6 facilitates this timetree inference by providing a graphical user interface (GUI) to specify the phylogeny and calibration constraints step-by-step. This version also contains enhanced algorithms to search for the optimal trees under evolutionary criteria and implements a more advanced memory management that can double the size of sequence data sets to which MEGA can be applied. Both GUI and command-line versions of MEGA6 can be downloaded from www.megasoftware.net free of charge.
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With the arrival of the first golden jackal Canis aureus individual in Lithuania in February 2015, the Ministry of the Environment moved immediately to add the species to the country's list of species that may be hunted and in May 2015 published a draft order to list the species as invasive. Through extensive review of literature from across the range of golden jackal in Europe, the aim of this paper is to provide a balanced argument in support of the view that golden jackals arrived in the Baltic States as a result of natural spread and are thus not invasive. Alongside, arguments are also presented to support the view that golden jackals are not likely to have a significant impact on the Lithuanian environment beyond a potential reduction in red fox Vulpes vulpes numbers. Accompanying, a summary of official and media reactions to the arrival of golden jackal is presented and a set of conclusions delivered that could assist in the ongoing debate in Lithuania.
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