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Reproduction of the golden jackal (Canis Aureus Moreoticus i. Geoffroy Saint Hilaire, 1835) in Julian Pre-Alps, with new data on its range expansion in the high-adriatic hinterland (Mammalia, Carnivora, Canidae)

Authors:
  • Museo Friulano di Storia Naturale
  • Progetto Lince Italia
  • Museo Friulano di Storia Naturale, Udine, Italy

Abstract and Figures

REPRODUCTION OF THE GOLDEN JACKAL (CANIS AUREUS MOREOTICUS I. GEOFFROY SAINT HILAIRE, 1835) IN JULIAN PRE-ALPS, WITH NEW DATA ON ITS RANGE-EXPANSION IN THE HIGH-ADRIATIC HINTERLAND (MAMMALIA, CARNIVORA, CANIDAE) Riassunto. Riproduzione dello sciacallo dorato (Canis aureus moreoticus I. Geoffroy Saint Hilaire, 1835) nelle Prealpi Giulie, con nuovi dati sulla sua espansione areale nell'entroterra alto-adriatico (Mammalia, Carnivora, Canidae). Vengono presentati alcuni dati sulla recente espansione dello sciacallo dorato Canis aureus moreoticus I. Geoffroy Saint Hilaire, 1835, nelle Prealpi italo-slovene, aggiornando le conoscenze sulla distribuzione della specie nell'entroterra Alto-Adriatico. In quest'area lo sciacallo ha recentemente aumentato la sua presenza, con varie evidenze che indicano la stabilizzazione dell'area di influenza di alcuni gruppi familiari sia in Italia, sia in Slovenia. Dal 2003, infatti, questo canide ha stabilizzato la posizione di alcuni punti tradizionali di richiamo vocale in varie zone delle Prealpi Giulie, riproducendosi con certezza almeno nel 2007. Questo quadro sembra congruente con una nuova blanda tendenza all'espansione dell'areale della specie, che sembra comprendere il Carso e le Prealpi Giulie italo-slovene. La conservazione di questa fragile popolazione trans-nazionale di sciacalli dorati sembra essere interamente dipendente da campagne di sensibilizzazione del pubblico venatorio, sia in Italia, sia in Slovenia. Summary. Data on the recent expansion of the golden jackal Canis aureus moreoticus I. Geoffroy Saint Hilaire, 1835, in the Italian-Slovenian Pre-Alps are presented, updating the knowledge on the distribution of this species in the High Adriatic hinterland. In this area, the species has recently increased its presence, with evidence of the range-stabilization of local family-groups both in Italy and in Slovenia. Since 2003 this canid has established some traditional howling spots in various zones of the Julian Pre-Alps, reproducing with certainty at least in 2007. This picture seems to be congruent with a new bland trend of range expansion of the species that seems to encompass the whole Italian-Slovenian Karst and the adjacent Italian-Slovenian Julian Pre-Alps. The conservation of this trans-national fragile population of golden jackals seems to be entirely dependent to public awareness campaigns directed to the hunters, both in Italy and in Slovenia.
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Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 169
Luca Lapini, Paolo Molinari, Luca Dorigo, Giovanni Are, Paola Beraldo
REPRODUCTION OF THE GOLDEN JACKAL
(CANIS AUREUS MOREOTICUS I. GEOFFROY SAINT HILAIRE, 1835)
IN JULIAN PRE-ALPS, WITH NEW DATA ON ITS RANGE-EXPANSION
IN THE HIGH-ADRIATIC HINTERLAND (MAMMALIA, CARNIVORA, CANIDAE)
Riassunto. Riproduzione dello sciacallo dorato (Canis aureus moreoticus I. Geoffroy Saint Hilaire, 1835) nelle
Prealpi Giulie, con nuovi dati sulla sua espansione areale nell’entroterra alto-adriatico (Mammalia, Carnivora,
Canidae).
Vengono presentati alcuni dati sulla recente espansione dello sciacallo dorato Canis aureus moreoticus I. Geoffroy
Saint Hilaire, 1835, nelle Prealpi italo-slovene, aggiornando le conoscenze sulla distribuzione della specie
nell’entroterra Alto-Adriatico. In quest’area lo sciacallo ha recentemente aumentato la sua presenza, con varie
evidenze che indicano la stabilizzazione dell’area di influenza di alcuni gruppi familiari sia in Italia, sia in
Slovenia. Dal 2003, infatti, questo canide ha stabilizzato la posizione di alcuni punti tradizionali di richiamo
vocale in varie zone delle Prealpi Giulie, riproducendosi con certezza almeno nel 2007. Questo quadro sembra
congruente con una nuova blanda tendenza all’espansione dell’areale della specie, che sembra comprendere il
Carso e le Prealpi Giulie italo-slovene. La conservazione di questa fragile popolazione trans-nazionale di sciacalli
dorati sembra essere interamente dipendente da campagne di sensibilizzazione del pubblico venatorio, sia in Italia,
sia in Slovenia.
Summary. Data on the recent expansion of the golden jackal Canis aureus moreoticus I. Geoffroy Saint Hilaire,
1835, in the Italian-Slovenian Pre-Alps are presented, updating the knowledge on the distribution of this species in
the High Adriatic hinterland. In this area, the species has recently increased its presence, with evidence of the
range-stabilization of local family-groups both in Italy and in Slovenia. Since 2003 this canid has established some
traditional howling spots in various zones of the Julian Pre-Alps, reproducing with certainty at least in 2007. This
picture seems to be congruent with a new bland trend of range expansion of the species that seems to encompass
the whole Italian-Slovenian Karst and the adjacent Italian-Slovenian Julian Pre-Alps. The conservation of this
trans-national fragile population of golden jackals seems to be entirely dependent to public awareness campaigns
directed to the hunters, both in Italy and in Slovenia.
Keywords: Canis aureus, range-expansion, North-Eastern Italy, North-Western Slovenia.
INTRODUCTION
The first data on the presence of the golden jackal Canis aureus moreoticus in Slovenia
were published by BRELIH (1955), who reported about the sighting of various jackals packs,
some of these in the surroundings of Kobarid, in Julian Pre-Alps. At the beginning of the
1950’s in northern Slovenia three specimens were shot, two near the wood of Razor, near
Vrhnika (Ljubljana), and one third near Smast (Kobarid). According to BRELIH (1955), only
one of the first two jackals was stuffed and preserved in the Museum of Bistra (Vrhnika,
Ljubljana) (probably the specimen in fig. 1). In the same period, the early 1950’s, groups of
golden jackals probably reached also various zones of north-eastern Italy, particularly in the
wild Catchment of the River Natisone (Julian Pre-Alps, Udine Province). These data,
usually referred to sightings of “wolves packs”, were sometimes published also by local
170 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
Italian newspapers (see for example the “Gazzettino” of 28 October 1956).
Nevertheless, this first expansion of the golden jackal to the north of its Balkan range
seemed end in the following years, apparently without particular consequences.
A second, impressive, expansion of the species started in the early 1980’s of the XX
Century, when the golden jackal colonized the Istrian Peninsula, expanding its Balkan
range up to NE Italy, Austria, Hungary, probably due to a strong increase of its Dalmatian
and Bulgarian populations (DEMETER, 1984; MILENKOVIC, 1987; LAPINI & PERCO, 1988,
1989; RALLO, 1989; SPASSOV, 1989; HOI-LEITNER & KRAUS, 1989; KRYšTUFEK &
TVRTKOVIC, 1990; KRYšTUFEK, 1991; DEMETER & SPASSOV, 1993; KRYšTUFEK et al., 1997,
BAUER, 2002).
In this period, the spreading of the species to the North followed various paths of
expansion; some of these encompassed the Karst and part of Julian Pre-Alps, various zone
of the Republic of Slovenia, and the adjacent Italian mountains and lowlands.
The first reliable data on the presence of the golden jackal in north-eastern Italy was
published only in the later 1980’s (LAPINI & PERCO, 1988), when it was possible to
ascertain the reproduction of the species near Udine. In this zone a young (in 1985, fig. 2)
and a big pluriparous female (in 1987, LAPINI & PERCO, 1988, 1989) were shot, while
another young was killed by cars on an highway (in 1985). The prosecution of the
researches permitted to gather further information on “Italian” jackals, that surprisingly
turned out to be present in north-eastern Italy at least from 1984, when one of the two
specimens sighted near S. Vito di Cadore (Belluno Province) was captured by a game-
Fig. 1. Male golden jackal shot in the wood of Razor (Vrhnika, Ljubljana) in January-February of the 1953 (Unla-
belled specimen from the Museum of Bistra, Ljubljana, Photo L. Lapini). The data of this specimen, together with
various sightings from Julian Pre-Alps, were firstly published by Savo BRELIH (1953).
Fig. 1. Sciacallo dorato maschio abbattuto nel bosco di Razor (Vrhnika, Ljubljana) nel Gennaio-Febbraio del 1953
(Esemplare privo di cartellino del Museo di Bistra, Ljubljana, Foto L. Lapini). I dati di questo esemplare, assieme
a varie segnalazioni delle Prealpi Giulie, furono pubblicate per la prima volta da Savo BRELIH (1953).
Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 171
keeper. It was confused with a big fox and the datum was published only nine years later,
when one of us (L. L.) saw a photo of the specimen, exposed in the game-keeper offices of
Belluno Provincial Administration (this picture was published by LAPINI et al., 1993). In
this period, at least up to the beginning of the 1990’s, in these Pre-Alpine areas a
reproductive family-group of golden jackals probably dwelled (see for example LAPINI,
1994). On 25 June 1992, in fact, a two years-old golden jackal was killed by cars in the
surroundings of the little town of Preganziol (Treviso Province), that till now constitute the
south-western limit of its expansion in northern Italy (LAPINI et al., 1993). In the following
years its presence was also documented in the Karst around Gorizia (LAPINI et al., 1996;
DELLA PIETÀ, 1998) (see also Fig. 3). A complete review of the information about the
distribution of the golden jackal in Italy was published in 2003 (LAPINI, 2003), while a
popular synthesis of the same data was also made by SPAGNESI & DEMARINIS (2002).
The expansion of the Balkan range of the species seemed to stop around at the end of
the 1990’s of the XX Century, probably due both to the occasional hunting pressures in
Italy, Austria and Slovenia and following the oscillation of the density of Croatian
populations (Krofel, in litteris).
During its last expansion, however, the species has established new reproductive
Fig. 2. A five to seven months old golden jackal born in the wild and shot in the surroundings of Udine, north-eastern
Italy, in September 1985. Note that the specimen was at the end of the milk dentition, showing the double canine
tooth-pattern typical of this age (Photo L. Lapini, P. Gori Collection, Terenzano, Udine). This is probably the first
golden jackal reproductive data available from north-eastern Italy (LAPINI & PERCO, 1988, 1989).
Fig. 2. Un giovane sciacallo dorato di 5-7 mesi nato in natura ed abbattuto nei dintorni di Udine, Italia nord-
orientale, nel Settembre 1985. Si noti che l’esemplare era alla fine della dentizione da latte, mostrando il tipico
doppio canino tipico di questa età (Foto L. Lapini, Collezione P. Gori, Terenzano, Udine). L’immagine si riferisce
probabilmente al primo dato riproduttivo disponibile per l’Italia nord-orientale (LAPINI & PERCO, 1988, 1989).
172 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
households in Hungary, where it is now relatively common in some areas of the country
(LANSKI et al., 2007). The spontaneous restoration of its populations in the Carpathian
Basin at the end of the XX Century constitute interesting news, because in these zones the
native jackals underwent to the extinction about one hundred years ago (DEMETER, 1984;
DEMETER & SPASSOV, 1993).
In Austria, moreover, the species has recently began to reproduce in the National Park
of Neusiedlersee, with a family-group probably arrived from Hungary (HERZIG-STRASCHIL,
2008).
In Slovenia the species seems to be always concentrated at the border between Trieste’s
Karst and northern Istria (KROFEL, 2008a), showing recent trends to the colonization of the
North of the country. A young female was recently shot in the Savinja Valley (KROFEL &
POTOčNIK, 2008) and there are new recent records of territorial groups in the Ljubljansko
Barje (KROFEL, 2009). Jackal penetration in Slovenia, however, seems still to be strictly
dependent to Croatian populations, recently monitored only by KROFEL (2007, 2008b).
In Italy the species seems to have recently increased its presence in Julian Pre-Alps,
Fig. 3. Two golden jackals photographed in the polje of the Lake of Doberdò (Community of Doberdò del Lago,
Gorizia, July 1997) (Photo A. Scarpa).
Fig. 3. Due sciacalli dorati ripresi nel polje del lago di Doberdò (Doberdò del Lago, Gorizia, Luglio 1997) (Foto
A. Scarpa).
Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 173
where it is regularly confused with the wolf (or with red foxes in moulting or affected by
sarcoptic mange). However, apart from the already quoted data published by BRELIH (1955)
up to now there are few and uncertain data from Julian Pre-Alps. At the end of XX Century
it was possible to collect some data about the presence of wild canids on these mountains -
snow traces on Mount Kolovrat (Drenchia, Udine Province) and a sighting on the Mount
Matajur (Savogna, Udine Province)- but it was never possible to ascertain their identity
without any doubt (tab. 1). Only in 2003 it was possible to obtain new information about
the presence of the golden jackal along the Italian-Slovenian border. The verification of
these and other data, mainly obtained in a preliminary survey performed between 2003 and
2009, constitutes the subject of the present paper.
MATERIAL AND METHODS
For our survey we used a range of methods performed following an opportunistic rather
then a systematic strategy, but integrated between them to obtain a better resolution of the
information. These were the methods employed:
Systematic verification of all the available sightings, also when they were referred to
wolves. Most hunters, game keepers and local people are clearly not able to distinguish the
golden jackal from the wolf (and often also the jackal from the red fox). This fact is easily
demonstrable from the comparison between our results and the affirmations of hunters,
local people and newspapers, that in most cases consider golden jackals as “little wolves”.
There are many proofs of this, both in Italy and in Slovenia. In this respect, however, the
short Slovenian article on a “Mali Volk (=little wolf)” (ANONYMOUS, 1992) quoted by
LAPINI et al. (1993) is particularly clear. This is surely referred to a particularly confident
golden jackal that in 1992 dwelt in and around the small village of Gropada, Padriciano
Community (Trieste). Also when it was shot (and destroyed) by a local hunter it remained
“a little wolf”, in spite of the fact that our research group had already established its identity
thanks to numerous detailed sightings (see again LAPINI et al., 1993).
Localization and verification of howling spots. The information about the position of the
howling spots were obtained occasionally, or thanks to the indication of researchers,
hunters or local people, that in all cases had referred on howling of “wolves”. Howling
spots were usually verified and attributed to jackals by means of photo-trapping, or by other
naturalistic methods, like the search of footprints or other signs of jackal presence (hairs,
droppings, etc.).
Acoustic stimulation. The jackal-howling method was performed both with empiric
methods (sometimes also by simple vocal stimulations) and following the indication in
GIANNATOS (2004) and GIANNATOS et al. (2005), also thanks to specific advice by the same
Author. His standard method (already utilized also in Hungary and in Dalmatia respectively
by LANSKI et al., 2007 and KROFEL, 2008b) consists in play-back sessions composed by six
174 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
emission of 30 sec. of pre-recorded howls repeated every 5 min., always changing the
direction of the emissions to cover 360° of the surveyed territory. These sessions were
performed at an intensity of 15-20 Watts, no more than one time per month in each of the
surveyed localities. Golden jackals, in fact, rapidly learn to avoid sites that are
overexploited as play-back stimulation point (Giannatos, in litteris). The intensity of our
emissions can be heard within a radius of about 2 km from the emission points, particularly
in good weather conditions. If the emissions are performed at the crossing points of a 4x4
km grid overlapped to a map of the surveyed area it is possible to cover large areas in short
times. For the moment, however, our survey was not systematic, but opportunistically
directed to some particular situation or zones.
Utilization of photo-traps. This method, largely employed in the U. S. A., in the tropics, in
Turkey, in the Balkans and in Switzerland to study nocturnal carnivores, was firstly
introduced in north-eastern Italy in 1998 by one of us (P. M.), and after it was employed by
various researchers of the University of Udine in their works on big carnivores (see for
example FATTORI & ZANETTI [2009]). This is a quite expensive method and in our
researches on the golden jackal it was performed at random along big game mammals
paths, or in proximity of the surveyed howling spots, mostly in sites that were baited with
caproic acid (= n-Hexanoic Acid), or/and meat and pig’s fat. The utilize of n-Hexanoic
Acid, a canids-directed specific attractant, was utilized on the golden jackal for the first
time.
Study of specimens obtained from road-mortality or by means other casualties. The
examination of all the available jackals has been performed with standard techniques, in
order to establish the causes of their death, to search for rests of alimentation in their guts
and faeces, to obtain data about their physiologic and health status (body size, sex,
estimated age, nutrition and reproductive status, presence of ecto and endo-parasites, etc.).
RESULTS
Between 2003 and 2009 only a little part of our field efforts gathered some data, about
less than 10% of the whole field efforts. Our positive results are summarized in tab. I, and
they may be commented as follow.
Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 175
Tab. 1. Positive results of 2003-2009 survey activities. In the table have been shown also some data of 1993 and
2005 already quoted in this paper (see the Introduction).
Tab. 1. Risultati positivi delle attività di monitoraggio 2003-2009. Nella tabella sono inseriti anche alcuni dati del
1993 e del 1995 già citati in questo lavoro (si veda l’Introduzione).
176 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
The verification of the available sightings has been conducted with a discrete systematic
effort, but only in rare cases we were able to gather reliable information on the jackals, i.e.
to confirm the species. During these verification, on the contrary, it was possible to confirm
that the totality of the witnesses -hunters, game-keepers and local people- regularly mistake
red foxes affected by sarcoptic mange (or in a problematic state of moult) for golden
jackals. The sighting of a true golden jackal, on the contrary, was always referred to as a
wolf, or a little wolf. This was proofed both with photo-trapping sessions and with the study
of the traces, confirming previous observation on this matter (see again LAPINI et al., 1993).
This erroneous and controversial perception of the golden jackal may be due to the fact that
its presence is still not traditional, neither in Italian and Slovenian humanistic culture, nor in
hunting and game-keepers traditions. On the contrary, wolves are a traditional presence
both in literature, folklore and hunting traditions of the high Adriatic Hinterland, in spite of
the fact that they are extinct in North-Eastern Italy at least from the Thirties of the XX
Century (the last wolf of these zones was captured in 1931 in the locality “Campo Bon,
Baita of Dosoledo”, Upper Comelico, Belluno Province: FOSSA, 1988), and that in Slovenia
they dwell only in the South of the country (Adamic, in KROFEL & POTOčNIK, 2008). There
are some exceptions to this rule, but they are very rare. The only available data on this
subject must be referred to some recent reports (photos and videos) of at least one
(vagrant?) wolf occurring on Hrušica and Pokljuka plateau, around to the Triglav National
Park (KROFEL, in litteris), or to a recent wolf skull collected in Val di Fiemme (North-
eastern Italy, Trentino Alto Adige Region, Trento Province) and studied by one of us (L. L.)
in May-June 2009. Also the bio-molecular confirmation of a sporadic Balkan-wolf presence
in Carinthia (near St. Veit: ANONYMOUS, 2009), for the moment agrees with a similar
picture of absolute exceptionality. In Friuli Venezia Giulia and Veneto Region, however, at
present there are no proofs of the presence of the wolf (in spite of the unverified data
published by FILACORDA, 2006), and in a first approach all the sightings attributed to
wolves must be referred to golden jackals and verified by photo-trapping sessions, play-
back campaigns, or genetics.
The survey of jackal howling-spots has surprisingly revealed that some of these were
regularly utilised since at least five-six years, surely having a traditional importance in the
social-behaviour and in the territorial economy of some family-groups. It seems to be
probable that these traditional points of vocal stimulation serve to mark the border -or the
core- of the area of influence of a pack (DEMETER & SPASSOV, 1993). In the surveyed area, a
single jackal-howl has a 5-6 sec. mean duration and it is usually repeated once every
minute, sometimes even for one hour (or longer). The best period to hear these single
vocalizations is around January and February, but they can be heard in other periods of the
year too. Choruses, on the contrary, have been heard for the moment only in late summer
(border of the Karst).
Acoustic stimulation. The jackal-howling method has been gathering good results also in
recently colonized areas, such as Hungary (LANSKI et al., 2007), but in the surveyed area
jackals rarely responded to play-back stimulations thereby providing only patchy
Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 177
information (see also KROFEL, 2009). This may be probably due to the rarity of reproductive
and established family-groups in the surveyed areas, which are the ones that tend to
vocalize (KROFEL, in litteris). In the golden jackal, in fact, the howls have a territorial
function and in marginal populations they are very rarely utilized. The responses obtained
in Italy, moreover, where mostly made up by individual howls (Julian Pre-Alps) and only
rarely by collective choruses (border of Italian Karst). Choruses, however, are particularly
important because they usually indicate the presence of a reproductive family-group.
Curiously, for the moment, we have obtained proofs of the reproduction of the golden
jackal only in the Julian Pre-Alps, where it was never possible to obtain collective
responses or choruses. It must however be noted that in our preliminary play-back survey
our field efforts were mostly concentrated on the Julian Pre-Alps, therefore increasing the
chances to detect reproduction compared to other sites.
Photo trapping. Photo-traps were particularly useful to ascertain the identity of a jackal
near Bovec (northern Slovenia, fig. 4) and that of some howling specimens in the
Community of Pulfero (Udine, Italy). The utilisation of baited photo-traps has also
permitted to verify the reproduction of the golden jackal near one howling-spot localized on
Julian Pre-Alps. In September 2007, in fact, it was possible to obtain a portrait of a young
golden jackal that seemed to be 5-7 months old. Its photo was submitted to various jackal
experts, included Giorgios Giannatos (University of Athens), who has confirmed that the
specimen was a young, surely born in the surroundings of the monitored howling-spot.
Fig. 4. A male golden jackal photo-trapped in February 2006 near Bovec (north-western Slovenia) (Photo P.
Molinari).
Fig. 4. Un maschio di sciacallo dorato ripreso da foto-trappole nel febbraio 2006 vicino a Bovec (Slovenia nord-
occidentale) (Foto P. Molinari).
178 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
In our preliminary field experience with attractants the n-Hexanoic Acid seemed to be a
good attractant for the golden jackals, but no more than fresh meat, pig’s fat or canned fish.
These last baits, however, are surely less specific, attracting a lot of other species. During
our generic field-experiments, in fact, it was possible to ascertain the presence of several
un-target mammals (the yellow-necked wood mouse, the wood mouse, the striped field
mouse, the brown bear, the wild cat, the wild boar, the red fox, the pine marten, the stone
marten, the badger, the roe deer, the western hedgehog, etc.), while the exclusive utilisation
of the n-Hexanoic Acid seemed more effective in attracting mainly canids (see fig. 5). From
our experiences, however, it seems to be preferable to utilize mixed baits, allowing to
obtain more information on the whole local mammal community.
The study and dissection of dead animals was performed on a single sub-adult male
killed by cars. It was collected on 25 February 2009 along a highway near to the village of
Sistiana (Duino-Aurisina Community, Trieste Province) by agents of the Italian Forestry
Fig. 5. Two red foxes photo-trapped by a deer-cam during the olfactory-exploration of a plant baited with n-
Hexanoid Acid. The attractant was sprayed on a little cortical incision practiced on the small tree (10 September
2006, loc. Comesta, Tramonti di sopra, Pordenone) (Photo L. Lapini-M. Pavanello-R. Raue-L. Dorigo).
Fig. 5. Due volpi riprese da una fototrappola di tipo deer-cam durante l’esplorazione olfattiva di una pianta
innescata con Acido Esanoico. L’esca è stata spruzzata su una minuta incisione corticale praticata sulla piccola
pianta (10 Settembre 2006, loc. Comesta, Tramonti di sopra, Pordenone) (Foto L. Lapini-M. Pavanello-R. Raue-L.
Dorigo).
Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 179
Corps (CFS, Office of Biodiversity of Tarvisio) (fig. 6). The specimen was measured and
ecto and endo-parasites were searched and collected. They where then determined at the
species level by one of the Authors (P. B.). It was also possible to analyse the gut contents
of this jackal, with special attention to the identification of the prey-species ingested during
the two days preceding its death. Some tissues for the bio-molecular characterization of the
specimen were also preserved. The results of these activities are synthetically summarized
in tab. 2.
The examination of a live specimen caught in the wild it was carried out on the 30th of
April 2009. This jackal, a sub-adult male that had lost its tail (fig. 7), was caught by the
game-keepers of Venice’s Provincial Administration in the centre of the town of San Dona’
di Piave (Province of Venice). It was found entangled in a metallic fence of a private garden
in the city (fig. 7). It was released from the fence following a bland anaesthesia and after a
few hours it was released in the “Wood of Bandiziol”, a protected area in the Community of
San Stino di Livenza (Province of Venice) (fig. 7). From this golden jackal it was only
possible to obtain samples (droppings, blood and hairs) for its future bio-molecular
characterization.
CONCLUSION, DISCUSSION AND PERSPECTIVES
Our data show that the golden jackal is probably undergoing a range expansion in the
high Adriatic Hinterland, having surely colonised the Italian and Slovenian Julian Pre-Alps
with at least one reproductive family-group. The information collected so far is not
sufficient to allow to estimate their number, but jackals in this area seem to be still very rare
(perhaps 2-4 specimens). Nevertheless it is very likely that along the Italian-Slovenian
border there are at least two family-groups: the first (1) located along a North-South
oriented ellipse that encompasses the small town of Bovec, the village of Stupizza and the
North-Western slope of the Mount Matajur, and the second (2) located along another ellipse
that encompasses the area of the Vignano Wood, the village of Kozina and the Ospo-Risano
Valleys in neighbouring northern Istria (fig. 8). This preliminary picture, surely more than a
simple working hypothesis, results from considering the information deriving from (1)
sightings, (2) play-back sessions, (3) the study of traditional howling spots, (4) the use of
baited and un-baited photo-traps, (5) and the study of the distribution of recent road-kills
and hunting records (for these see also KROFEL, 2008a).
The study of the sub-adult male road-kill near Sistiana on 25 February 2009 also seems
to support this preliminary picture. This specimen is probably a 22-24 months old sub-adult
and was probably born at the border of Italian Karst. In South Europe the young males
usually leave their own family-group at about two year of age (Giannatos, in litteris,
unpublished data), while females usually remain with their own family for a longer time,
often becoming helpers (DEMETER & SPASSOV, 1993). For this reasons the presence of
females may indicate a trend to the range expansion (KROFEL & POTOčNIK, 2008), a process
that in the golden jackal may be sometimes ensured also by a single pregnant female.
180 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
Fig. 6. A sub-adult male about two years old road-killed in the surroundings of Sistiana (Duino-Aurisina
Community, Trieste, north-eastern Italy) on the 25th february 2009 (Photo CFS, Territorial Office for the
Biodiversity from Tarvisio, Udine).
Fig. 6. Maschio sub-adulto di quasi 2 anni investito da automobili nei dintorni di Sistiana (Duino-Aurisina,
Trieste, Italia nord-orientale) on 25 february 2009 (Foto Corpo Forestale dello Stato, Ufficio Territoriale per la
Biodiversità di Tarvisio, Udine).
The sub-adult without tail caught at San Dona’ di Piave (Province of Venice) on the 30th
April 2009, on the other hand, might indicate an under-estimation of jackal presence also in
the whole of north-eastern Italy. Indeed, it must be in fact noted that this new distributive
datum is in close proximity to a single datum of presence already published for the
neighbouring Province of Treviso (LAPINI et al., 1993) (fig. 8). Both these data might be
connected to a marginal reproductive population dwelling on Venetian Pre-Alps, that
utilizes the Piave River Valley as faunal corridor to penetrate into Venetian floodplain (see
the Introduction for some historic details on the golden jackal in the Province of Belluno).
In Italy, the species is nominally protected since 1997 (National Law 157/1997) and in
Slovenia since 2004 (KROFEL & POTOčNIK, 2008), but the sole legal protection it is not
enough. The golden jackal, indeed, is frequently shot during culling operations directed
toward the red fox, both in Italy and in Slovenia. Moreover the species has been regularly
confused with wolves and this increases the problems involved in its trans-national
monitoring. In this situation whereby misidentification is common, a better comprehension
of the golden jackal status might be ensured by non-invasive genetic-based researches
Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 181
Standard measurements
g 03521 htgiew latoT = P
mm 028 liat eht fo toor lasrod - pit muiranihR = CT
mm 072 liat eht fo toor
lasrod - pit liaT = C
mm 261 )walc tuohtiw( htgnel toof dniH = PP
mm 59 suhtaem citsuoca eht fo sesa
b - pit raE = O
Body
T = Maximum x minimum diameter of rigth and left testes 33x2,8 mm (both)
mm 9,561 )noilesneH - noihtanG( htgnel lasab olydnoC
mm 0,29 htdaerb citamogyZ
mm 46,13 seninac revo
htdaerb llukS
mm 68,65 sralom revo htdaerb llukS
mm 8,02 seninac reppu neewteb ecnatsid lasaB
mm 24,
48 )enips latalap - noihtang( htgnel latalap mumixaM
Skull
°5,64 elgna latibrO
Mandible length (center of the Condylus articularis - Mandibular tip) 128,8 mm
mm 63,74 htgieh dionoroC
Mandible
Max. length of the mandible (edge of the Condylus articularis – Mand. tip) 129,6 mm
Additional veterinary measurements
Shoulder height 550 mm Head circumference 313 mm
Neck circumference 245 mm Thoracic circumference 540 mm
mm 544 ecnerefmucric lanimodbA
mm 06 )dap latigid regnol eht fo pit - dap ratnalp fo esab( htgnel wap
tnorF
mm 45 )dap latigid regnol eht fo pit - dap ratnalp fo esab( htgnel wap dniH
mm 45 ,55 ,89 ,48
nemodba ,knalf ,redluohs ,kcab no sriah fo htgneL
Gut contents
Stomach About two hectograms of fresh fibrous meat without bones, feathers or hairs, with some dried
leaves taken from the substratum of a karstic wood
Intestine Nothing
Parasites (A: ectoparasites; B: endoparasites)
A Dermacentor reticulatus (Fabricius, 1794); Ixodes ricinus (Linnaeus, 1758). The first species is probably
signalled for the first time in Friuli Venezia Giulia Region.
B
In the small intestine (intestinum tenue) of the jackal, six specimens of Metagonimus yokogawai (Katsurada,
1912) -the smallest human fluke- were found. Mostly distributed in the Far East, this digenean trematode
occurs in Siberia, Manchuria, Japan, Korea, India (rare), China, Taiwan, The Philippines, Indonesia, Russia,
Romania, Bulgaria, the Balkan states, Israel and Spain. The life-cycle of this fluke includes at least two
intermediate hosts, first a mollusc and after a freshwater fish (mainly Cyprinidae). The infection (called
metagonimiasis) was linked to the ingestion of raw infected fish, and in humans it is typically due to the
consumption of low-quality Sushi. These data represent the first available information on the occurrence of
this trematode in Italy and also indicate that the studied jackal has surely eaten freshwater fishes
Tab. 2. Standard body measurements and gut contents of the sub-adult male killed by cars in the surrounding of
Sistiana (Duino-Aurisina, Trieste) on 25th February 2009. Additional veterinary measurements are also given, to
compare them with those published by KROFEL & POTOčNIK, 2008, together with some consideration about the
parasites collected on the studied jackal.
Tab. 2. Misure corporee standard e contenuto del tratto digestivo del maschio subadulto investito da automobili
nei dintorni di Sistiana (Duino-Aurisina, Trieste) il 25 febbraio 2009. Vengono fornite anche alcune misure
addizionali di tipo veterinario, per compararle con quelle pubblicate da KROFEL & POTOčNIK, 2008, assieme ad
alcune considerazioni sui parassiti raccolti sullo sciacallo studiato.
182 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
Fig. 7. A sub-adult male without the tail caught in the centre of San Dona’ di Piave (Province of Venice) on the 30th
April 2009. The specimen it was found entangled in a metallic fence in the city (above: photo P. Serafin). It was
rescued following a bland anaesthesia (below, on left: photo M. Cappelletto) and then released in the wild, within a
protected area near San Stino di Livenza (Province of Venice) (below, on right: photo M. Cappelletto).
Fig. 7. Un maschio sub-adulto senza coda catturato nel centro di San Dona’ di Piave (VE) il 30 aprile 2009.
L’esemplare era rimasto incastrato in una inferriata metallica cittadina (in alto: foto P. Serafin). Liberato grazie
ad una blanda anestesia (in basso, a sinistra: foto M. Cappelletto) è stato poi rilasciato in natura all’interno di
un’area protetta vicino a San Stino di Livenza (Venezia) (in basso, a destra: foto M. Cappelletto).
Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009 183
Fig. 8. Bibliographic (grey) and original (black, see also tab. 1) data on the distribution of Canis aureus in the
studied area. Small circles indicate surely ascertained presences (dead animals, photos, etc.), bigger circle indicate
ascertained reproductions; questionmarks (?) inscribed in the symbols indicate both uncertain data (most of
sightings, not surely attributed howls, etc.) and some reproductive uncertainty (in this case they are overlapped to
the bigger circles); dotted ellipses localize the presumed area of influence of territorial groups in the period 2003-
2009; asterisks (*) indicate the position of some howling points traditionally utilized by jackals in the same period.
Fig. 8. Dati bibliografici (in grigio) e informazioni originali (in nero, vedi anche tab. 1) sulla distribuzione di
Canis aureus nell’area indagata. I tondi più piccoli indicano presenze sicuramente accertate (animali morti, foto,
ecc.), i tondi grandi indicano riproduzioni accertate; punti interrogativi (?) inscritti nei simboli indicano sia dati
incerti (gran parte degli avvisamenti o degli ululati non sicuramente attribuiti), sia qualche incertezza
sull’avvenuta riproduzione degli animali (in questo caso essi sono sovrapposti ai tondi più grandi); le ellissi
punteggiate localizzano la presunta area di influenza di gruppi territoriali nel periodo 2003-2009; asterischi (*)
indicano la posizione di alcuni punti di stimolazione acustica tradizionalmente utilizzati dagli sciacalli nello
stesso periodo.
performed on hairs (or droppings) collected in the wild, also by the use of specific hair-
traps.
The conservation of the fragile and scattered jackal population occurring along the
politic boundary between Italy and Slovenia, however, needs a special trans-national
cooperation between Italian and Slovenian Politic-Administrative, Researchers and Hunter-
organisations, with precise management decisions in favour of this species.
184 Boll. Mus. civ. St. nat. Venezia, 60 (2009) 2009
It is also particularly important to increase the field efforts using jackal-howling surveys
coupled with photo-trapping to gather further information on the localisation of the Italian
and Slovenian jackal family-groups. Hair-traps should be used together with photo-
trapping, to obtain genetic samples that will allow to characterize all the jackals of these
zones by bio-molecular techniques. In these trans-national zones a similar strategy had been
already used for the brown bear, gathering interesting data about number and sex of the
bears living on these mountain-chains (see FATTORI & ZANETTI [2009] and SKRBIšEK et al.,
2008 for a trans-national synthesis of these activities).
In this early phase of the colonisation, however, the public awareness about the species
and its identification seems to be of primary importance both to increase the knowledge on
jackals distribution and to promote their conservation in the whole High-Adriatic
Hinterland. This front-line public-directed activity is crucial to avoid mistakes during fox
hunting (see LAPINI, 2003 and KROFEL & POTOčNIK, 2008), which is the main problem for
the conservation of the golden jackal in the whole High Adriatic Hinterland.
ACKNOWLEDGEMENTS
We want to thank Giorgios Giannatos (Athens, Greece) and Miha Krofel (Ljubljana,
Slovenia) for various useful exchanges of opinion and for their methodological and
bibliographic help. Special thanks to Massimiliano Rodolfi (CFS, Territorial Office for the
Biodiversity of Tarvisio) and to the public Administration of the Province of Udine
(Operational Unit for the Management of Naturalistic Resources) for their help in the study
of a specimen from road-mortality. The cooperation of P. Serafin and M. Cappelletto, game-
keepers of the Provincial Admnistration of Venice, was particularly important to examine
the jackal caught in the centre of San Dona’ di Piave (Venice). G. Canderan (Reana del
Roiale, Udine), M. Cassol (Sedico, Belluno), S. Filacorda (Treppo Grande, Udine), T.
Fiorenza (Udine), P. Gori (Terenzano, Udine), W. Grion (Capriva del Friuli, Gorizia), F.
Perco (Gabrovizza, Sgonico, Trieste), R. Peressini (San Lorenzo Isontino, Gorizia), M.
Pavanello (Tramonti di Sopra, Pordenone), E. Randi (ISPRA [ex INFS], Ozzano
nell’Emilia, Bologna), R. Raue (Tramonti di Sopra, Pordenone), E. Sbrugnera (Udine), A.
Scarpa (Ronchi dei Legionari, Gorizia) and T. Trilar (Ljubljana) gather some photos,
biologic materials, information or support in laboratory or field experiences. Thanks also to
the direction of the Friulian Museum of Natural History (Udine) that in the last 23 years has
enthusiastically encouraged our researches on the golden jackal. The English form of this
paper has been improved by L. Bonesi (Postdoct. Researcher at the Wild Cru, Oxford-UK
and at the University of Trieste, Italy).
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Authors’ addresses:
Luca LAPINI, Via dei Monti, 21, I-33034, Fagagna, Udine, ITALY;
e-mail: lucalapini@libero.it
Paolo MOLINARI, Via Diaz, 90, I-33018, Tarvisio, Udine, ITALY;
e-mail: p.molinari@wilcons.eu
Luca DORIGO, Corso Roma, 32, I-33097, Spilimbergo, Pordenone, ITALY;
e-mail: luca.scorpio@libero.it
Giovanni ARE, Via del Raboso Piave, 1, I-31050, Zenson di Piave, Treviso, ITALY;
e-mail: gioare@inwind.it
Paola BERALDO, University of Udine, Dept. of Animal Science, Section of Biology and Animal Pathology, Via
delle Scienze, 206, I-33100, Udine, ITALY; e-mail: paola.beraldo@uniud.it
Addendum: In summer 2009 the presence of the golden jackal was ascertained also in Val Pusteria-Pustertal
(Bolzano-Bozen Province, Alto Adige-Süd Tirol, Italy) on the basis of sure biological samples. At present this
valley is the Northernmost Italian site where the presence of the species has been ascertained. This indicates that
the expansion of the jackal in North-Eastern Italy is still in progression, also reinforcing the impression that in the
Dolomites its presence should be under-estimated.
A road-killed young female of golden jackal was collected on 10 December 2009 in the Municipality of Socchieve
(Province of Udine). This sample, examined thanks to the courtesy of S. Filacorda (Udine University), constitutes
a first confirmation of previous sightings for the same zone of Friulian Carnian Alps.
... Le cause di questa straordinaria espansione in tutta Europa sono state ormai oggetto di decine di studi, e sembrano poter essere ricondotte alla decimazione del lupo balcanico, particolarmente spinta verso la metà del secolo scorso (SPaSSoV & acoSta PankoV, 2019). Mancando questo grande canide, principale antagonista della specie in ampie zone dei Balcani e in parte del Caucaso, lo sciacallo ha iniziato una imponente migrazione verso Nord e Nord Ovest, arrivando a Caporetto/Kobarid (oggi Slovenia) già all'inizio degli anni '50 del XX secolo (laPini et al., 2009). Un film già visto, che ricorda da vicino quanto accaduto in Nord America tra coyote e lupo grigio, sterminato con le armi da fuoco dai coloni americani tra '700 e '800 (si veda la bella sintesi di cellini, 2020). ...
... Lo studio di Canis aureus nella particolare situazione italiana, ancora in piena fase di colonizzazione, si svolge sovrapponendo metodi differenti fra loro complementari (laPini et al., 2009;laPini, 2009laPini, , 2010. Per quanto FuSillo & laPini (2016) abbiano proposto metodi bio-acustici standardizzati per coprire ampie aree in poco tempo, dove le presenze del canide sono ancora sporadiche è necessario muoversi in maniera opportunistica, come viene ancora fatto in tutta l'Italia settentrionale (laPini et al., 2009(laPini et al., , 2011(laPini et al., , 2018laPini, 2019). ...
... Lo studio di Canis aureus nella particolare situazione italiana, ancora in piena fase di colonizzazione, si svolge sovrapponendo metodi differenti fra loro complementari (laPini et al., 2009;laPini, 2009laPini, , 2010. Per quanto FuSillo & laPini (2016) abbiano proposto metodi bio-acustici standardizzati per coprire ampie aree in poco tempo, dove le presenze del canide sono ancora sporadiche è necessario muoversi in maniera opportunistica, come viene ancora fatto in tutta l'Italia settentrionale (laPini et al., 2009(laPini et al., , 2011(laPini et al., , 2018laPini, 2019). ...
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Riassunto-foto-trappolaggio e jackal-howling sono stati impiegati in maniera opportunistica per studiare le rade presenze di sciacallo dorato (Canis aureus) disperse su diverse catene montuose della Provincia di Belluno. I risultati per ora confermano un'ampia distribuzione montana della spe-cie, con la presenza di almeno un gruppo riproduttivo territoriale insediato sui monti del Comelico (Comune di Santo Stefano di Cadore). Questi risultati sono poi stati confrontati con le principali conoscenze su questo raro canide in Italia, al fine di valutarli correttamente dal punto di vista con-servazionistico, scientifico e gestionale. Parole chiave: sciacallo dorato, Canis aureus, Comelico, Provincia di Belluno, Italia nord-orientale. Abstract-camera-trapping and jackal-howling techniques had been opportunistically employed to study the scattered presences of golden jackals (Canis aureus) on various Mountain-Chains of the Province of Belluno. The results so far confirm a wide mountain distribution of the species, with at least one reproductive territorial group dwelling on Comelico mountains (Santo Stefano di Cadore Municipality). These results have been then discussed within the knowledge about this rare wild dog in Italy, in order to correctly evaluate them from a protection, scientific and management point of view.
... Additional natural definitive hosts (most records as M. yokogawai): (i) mammals: European jackal Canis aureus moreoticus Saint-Hilaire (Italy [51]); C. familiaris (Croatia and Slovenia [6][7][8]25]; Russia [37,38,85]; Ukraine [23,39]); red fox Vulpes vulpes (L.) (Austria [31]; Serbia [57,72]; Slovenia [78]; Ukraine [39]) (Carnivora: Canidae); domestic cat Felis catus L. (Slovakia [99]; Turkey [16] (as M. ciureanus); Ukraine [17,23,46,59]) (Carnivora: Felidae); (ii) birds: whitetailed eagle Haliaeetus albicilla (L.) (Czech Republic [84]; Romania [15]); black kite Milvus migrans (Boddaert) (Accipitriformes: Accipitridae) (Romania [15]); European herring gull Larus argentatus Pontoppidan (Charadriiformes: Laridae) (Bulgaria [95]; Ukraine [52,53]); white stork Ciconia ciconia (L.) (Ciconiiformes: Ciconiidae) (Bulgaria [95]); purple heron Ardea purpurea L. (Ukraine [10,86]); black-crowned nightheron Nycticorax nycticorax (L.) (Pelecaniformes: Ardeidae) (Ukraine [10,86]); Dalmatian pelican Pelecanus crispus Bruch (Bulgaria [95]; Croatia and Slovenia [6][7][8]25]); great white pelican Pelecanus onocrotalus L. (Pelecaniformes: Pelecanidae) (Romania [15]); glossy ibis Plegadis falcinellus (L.) (Pelecaniformes: Threskiornithidae) (Bulgaria [95]; Croatia and Slovenia [6][7][8]25]); pygmy cormorant Microcarbo pygmaeus (Pallas) (Romania [15]); great cormorant Phalacrocorax carbo (L.) (Suliformes: Phalacrocoracidae) (Poland [44]; Ukraine [10]). ...
... Distribution and records of adults and metacercariae (indicated by asterisk) (Fig. 4): Austria [31], Bulgaria* [3,26,42,66,70,95], Croatia (Neretva River delta [25]), Czech Republic [84], Hungary* [12,64], Italy [51], Poland [44], Romania* [13][14][15], Russia (?) (Rostov Oblast [85]), Serbia* [11,19,72], Slovakia* [71,91,[97][98][99][100], Slovenia [78], Turkey [16] (as M. ciureanus from Sapanca), Ukraine* [10, 17, 23, 37-39, 46, 59, 86], former Yugoslavia -Croatia and/or Slovenia [6][7][8]. ...
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The heterophyid trematode Metagonimus romanicus (Ciurea, 1915) (Digenea) is redescribed on the basis of type material from domestic dogs ( Canis familiaris ) in Romania, vouchers from experimentally infected cats ( Felis catus ) and adults recovered from golden hamsters ( Mesocricetus auratus ) infected with metacercariae from scales of chub ( Squalius cephalus ) and common nase ( Chondrostoma nasus ) (Cypriniformes: Leuciscidae) in Hungary. This trematode, endemic to Europe and neighbouring regions (northwestern Türkiye), was previously misidentified as M. yokogawai (Katsurada, 1912), a zoonotic parasite of humans in East Asia. However, the two species differ considerably both genetically and morphologically, e.g ., in the position of the ventral sucker, the presence of the prepharynx, the anterior extent of the vitelline follicles and the posterior extent of the uterus. Metagonimus ciureanus (Witenberg, 1929) (syn. Dexiogonimus ciureanus Witenberg, 1929), described from domestic cats and dogs in Israel, is a valid species distributed in the Middle East and Transcaucasia, which is also confirmed by molecular data. It differs from all Metagonimus species, including M. romanicus , in having symmetrical testes instead of the oblique testes of the other congeners. The zoonotic significance of M. romanicus and M. ciureanus is unclear, but appears to be low in Europe, mainly because raw or undercooked, whole fish with scales are generally not consumed. Accidental infection of fishermen by metacercariae in the scales when cleaning fish is more likely, but has never been reported. Remains of cyprinoids with scales infected with metacercariae of Metagonimus spp. can be an important natural source of infection for dogs, cats, and other carnivores, which can serve as a reservoir for these parasites.
... La raccolta di informazioni secondo i protocolli di Hatlauf et al. (2016) costituisce la base dei monitoraggi in tutti i paesi europei da poco colonizzati da Canis aureus. Nelle prime fasi della colonizzazione del nostro paese da parte del canide il confronto tra metodi opportunistici (Lapini, 2009(Lapini, -2010Lapini et al., 2016Lapini et al., , 2018 e metodi sistematici estensivi (Caboni, 2013) ha indicato che i primi restituivano la migliore rappresentazione della realtà distributiva, allora in una fase precoce di definizione nell'Italia nord-orientale. La presenza di gruppi riproduttivi territoriali della specie nel nostro paese viene quindi ancora ricercata con criteri opportunistici e confermata con le metodiche bio-acustiche proposte da Giannatos nel 2004 e perfezionate l'anno successivo (Giannatos et al., 2005), che hanno una particolare efficienza e risoluzione nel corso dell'estate (Hatlauf et al., 2016). ...
... La comunità di parassiti legati allo sciacallo dorato italiano non è ancora molto conosciuta, ma il piccolo canide sicuramente ospita alcuni endo-parassiti piuttosto rari nel nostro paese. Uno di questi è Metagonimus yokogawai (Katsurada 1912), un piccolo trematode digeneo per la prima volta rinvenuto in Italia nell'intestino di uno sciacallo dorato del Carso triestino da P. Beraldo, parassitologa dell'Università di Udine (Lapini et al., 2009). Nonostante ciò, gli sciacalli italiani sembrano ospitare una comunità di endo-parassiti piuttosto povera. ...
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Riassunto Gli Autori fanno una breve panoramica delle conoscenze sullo sciacallo dorato in Italia, aggiornandola a fine settembre 2021. La specie è attual-mente diffusa in tutta l'Italia settentrionale, a Sud almeno fino alla Provincia di Ravenna. In questa vasta zona della Penisola Italiana si stima siano ormai presenti 196-250 esemplari suddivisi in almeno 37-47 gruppi riproduttivi territoriali. La sorveglianza sanitaria di questi animali sembra per ora indicare buone condizioni di salute delle popolazioni. In Italia la specie non solleva forte allarme sociale, nonostante locali sospetti di conflitto con la zootecnia e l'attività venatoria. In Italia la specie è integralmente protetta dalla LN 157/92 e per il momento gode di discreto apprezzamento popolare. In questo paese la specie è fortemente antropofila sia dal punto di vista ambientale, sia trofico. I suoi principali problemi di conservazio-ne in questo paese sono gli investimenti stradali e il bracconaggio, esercitato sia con le armi da fuoco, sia con pesticidi e la competizione intra-guild con il lupo. La sua espansione verso Sud potrebbe essere limitata proprio dall'equilibrio con quest'ultimo. Abstract An updated overview about Canis aureus in Italy The Authors make an updated overview about Canis aureus in Italy summarizing all the data available up to September 2021. At present the species is distributed in the whole northern Italy, to the South reaching at least the Province of Ravenna. In this wide area of Italian Peninsula it was possible to estimate the presence of about 196-250 specimens, subdivided in at least 37-47 reproductive territorial groups. The health surveillance of Italian jackals up to now seems to indicate a good sanitary condition of the populations from northeastern Italy. In Italy the species does not cause strong social alarm, despite suspected overestimated local conflicts with agriculture, livestock and game species. It is nominally protected by Italian National Law 157/192 and for the moment it enjoys some popular appreciation. In the whole country the species is highly anthropophilic both from environmental and trophic point of views. The main conservation problems of Canis aureus in Italy are road accidents and poaching, this last conducted with weapons, traps and poisons, and the intra-guild competition with grey wolves. Its further expansion to the South in Italy may be limited in the future by ecological balance with the latter. Premessa Il recente arrivo dello sciacallo dorato in Italia si inserisce nell'ampio quadro di conoscenze sulle penetrazioni fauni-stiche post-glaciali da oriente. La faina (Martes foina), per fare soltanto un esempio, è comparsa in Europa occidenta-le soltanto negli ultimi 6.000-8.000 anni (Stubbe, 1993), probabilmente grazie alla neolitizzazione delle popolazioni indo-europee di queste zone. Tuttavia, mentre il percorso di questo mustelide sinantropico di provenienza medio-orien-tale è stato ricostruito grazie allo studio di reperti sub-fossili, l'arrivo di Canis aureus si svolge sotto i nostri occhi e rappre-senta un caso di studio privilegiato per comprendere le varia-bili biotiche e abiotiche che ne condizionano l'espansione. Questa è la ragione del grande interesse che la specie sta susci-tando anche in Italia, con un aumento esponenziale dei dati disponibili, pubblicati e non. Scopo di queste righe è fornire una prima incompleta siste-matizzazione di questa vasta trama di conoscenze, ancora poco limate, in rapida evoluzione e per certi versi ancora con-traddittorie. Esse si devono alle ricerche del Museo Friulano di Storia Naturale di Udine, che segue l'espansione della spe-*Dedicato a Fabio Perco (1946-2019), alla cui poliedrica sensibilità naturalistica si devono i primi dati su Canis aureus in Italia.
... As a result, populations began to recover, and the distribution expanded to Central and Western Europe (Spassov and Acosta-Panko 2019). Currently, the new range includes for example Hungary, Ukraine, Slovakia, Czechia, Austria, Switzerland, France, northern Italy, Germany, Poland, and the Baltic countries, while vagrants have been recorded in the Netherlands, Belgium, and Denmark (Bauer and Suchentrunk 1989, Hoi-Leitner and Kraus 1989, Zedrosser 1995, Koubek and Červený 2007, Plass 2007, Herzig-Straschil 2007, Lapini et al. 2009, 2011, Szabó et al. 2009, Fabbri et al. 2014, Zagorodniuk 2014, Slamka et al. 2017, Jirků et al. 2018, Stoyanov 2020, Böcker et al. 2023). ...
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In recent decades, the golden jackal (Canis aureus) has expanded its range westwards and northwards in Europe. In this study, we present genetic and morphological data on the first golden jackal collected north of the Arctic Circle. An adult male was shot after having been captured in a leg snare set for foxes near Sodankylä in Finland. It was a large-sized animal in good body condition, showing no signs of hybridization with other canids. The stomach contents included fish bones, likely obtained from an anthropogenic source, as well as remains of a galliform bird. This finding suggests that golden jackals are able to survive harsh winters, allowing them to extend their distribution range to the northernmost parts of Europe.
... The first confirmed occurrence of golden jackals in Slovenia dates back to 1952 (Brelih 1955) and two territorial families were recorded near Bevke, central Slovenia, in 2009(Krofel 2009). The golden jackals also spread to Italy, where they were recorded during the 1980s, with reproducing families confirmed in South Tyrol in 2009 (Lapini & Perco 1988, Lapini et al. 2009). Since that time, the number of jackal sightings throughout Europe has increased rapidly, however the number of documented breeding events outside the core contiguous breeding range is still relatively scarce. ...
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The permanent breeding range of the golden jackal (Canis aureus) in Europe was restricted to the Black Sea coast and Balkans in the 1960s. From the 1980s, a rapid and steady increase of the species occurrence has been documented throughout Europe. The observations of single individuals prevail, the proofs of breeding family groups are much more scarce. Here we present the second evidence of golden jackal breeding in Central Bohemia (Czech Republic) which took place near Dlouhá Lhota, about 50 km south of Prague, in 2022. Photographic evidence of adults and two cubs was made with the help of camera traps.
... Lapini (2006a) suggested that the slow colonization of Italy by the raccoon dog may occur through two independent routes, i.e., from NNE (Trentino-Alto Adige) and from ENE (Friuli Venezia Giulia). Moreover, the record from the floodplains of Torre stream suggests that rivers basins may serve as corridors for the invasion (as occurred with the expansion of the European wildcat Felis silvestris Schreber, 1777 and the golden jackal C. aureus Linnaeus, 1758 in north-eastern Italy, see : Lapini 2006b;Lapini et al. 2009) and therefore should be specifically monitored. ...
Article
The raccoon dog Nyctereutes procyonoides is an Asian canid species which has been introduced to Europe for fur farming. Local escapes and the animal subsequent dispersal have triggered the establishment of self-sustaining populations, particularly in Eastern European countries, but with several populations in Southern Europe as well. Despite being listed amongst the alien species of European concern (EU Regulation 1143/2014), data on raccoon dog distribution in Southern Europe and in particular in Italy are still scanty. In this work, we reviewed all the available data of raccoon dog in Italy. Only five confirmed occurrences are available, suggesting that in this country the species may still be at the beginning of the establishment process.
... La comunità di parassiti legati allo sciacallo dorato italiano non è ancora molto conosciuta, ma la specie sicuramente ospita alcuni endoparassiti piuttosto rari nel nostro paese. Uno di questi è Metagonimus yokogawai (Katsurada 1912), un piccolo trematode digeneo per la prima volta rinvenuto in Italia nell'intestino di uno sciacallo dorato del Carso triestino da P. Beraldo, parassitologa dell'Università di Udine (Lapini et al, 2009). Nonostante ciò, gli sciacalli italiani sembrano ospitare una comunità di endo-parassiti piuttosto povera. ...
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Premessa Ad ampia distribuzione euro-asiatica, lo sciacallo dorato (Canis aureus) è diffuso in Europa, Asia Minore, Medio Oriente (Egitto escluso), India e Asia sud-orientale almeno fino a Cambogia e Laos. Politipico, è stato suddiviso in numerose sottospecie, alcune delle quali sono state da poco elevate a rango specifico. Studi biomolecolari, filogeografici e la distribuzione dei suoi resti sub-fossili indicano chiaramente che lo sciacallo dorato è un invasore post-glaciale dell'Europa, arrivato dal Caucaso circa 8.000 anni fa (Spassov & Acosta Pankov 2019). Attualmente esso vive una fase di grande espansione in tutta Europa, originariamente partita da tre nuclei popolazionali: (I) la parte orientale del Caucaso, (II) la parte orientale della Transcaucasia e (III) le coste dalmate dei Balcani (Spassov & Acosta Pankov 2019). Questa impressionante espansione è sicuramente dovuta ad influenze antropiche (Trowborst et al. 2015), soprattutto dovuta alla decimazione del lupo in tutta Europa, culminata attorno agli anni '50 del XX secolo (Krystufek et al. 1997; Krofel et al., 2017). Il lupo, infatti, è il principale antagonista dello sciacallo dorato in natura. Foto M. Cappelletto (sn) L.Lapini (dx)
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Prin această teză de disertație s-a dorit realizarea unui studiu privind evaluarea prezenței speciei șacalului auriu (Canis aureus) prin două metode non-invazive: camera trapping și jackal howling. Activitatea desfășurată a acoperit o perioadă de șapte luni, începând cu octombrie 2019 până în aprilie 2020. Zona de studiu, cu o suprafață de 24 km2 este situată pe raza județului Vrancea, în Lunca Siretului Inferior, fiind suprapusă Rezervațiilor Naturale Pădurea Neagră și Pădurea Merișor�Cotul Zătuanului. Din cele două metode de colectare a datelor din teren, s-a putut identifica specia ca fiind prezentă în zona de studiu, fiind obținute și date privind distribuția, densitatea, numărul de indivizi, habitatul preferat și activitatea temporală. S-a folosit metoda pătratelor (1x1km) și metoda Kernel pentru a carta și descrie distribuția șacalului. Din cele două metode folosite s-a observat că șacalul este prezent în toată zona de studiu și aplicând Kernel 50% s-a estimat zona cu probabilitatea cea mai ridicată de a găsi șacal, găsindu-se în mijlocul și nordul zonei de studiu. Comparând distribuția spațială și temporală a șacalului cu alte specii (vulpe, bursuc, căprior, porc mistreț și iepurele de câmp), în ambele cazuri șacalul a avut cel mai mare grad de suprapunere cu iepurele de câmp. Densitatea șacalului estimată în zona de studiu (0,65 ind/km2 ), comparativ cu alte date bibliografice din diferite regiuni, se încadrează în mijlocul valorilor (0,11-1,7 ind/km2 ). Comparând categoriile de utilizare a terenurilor din toată aria de studiu, folosind metoda cu Kernel 50%, observăm că șacalul preferă zonele acoperite cu pădure. Acest studiu confirmă că cele două metode camera trapping și jackal howling, sunt eficiente în monitorizarea șacalului, deoarece ambele au permis, cu o rată de succes semnificativă confirmarea prezenței și identificarea zonelor nucleu utilizate de șacal în acest sector al râului Siret. De asemenea, abordarea standardizată a colectării și analizei datelor asigură reproductibilitatea temporală (urmărirea dinamicii populației de șacal), dar și spațială (implementarea în alte zone) a studiului.
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The golden jackal (Canis aureus) between Garda Lake and the city of Verona (Carnivora: Canidae). Camera-trapping and bio-acoustic techniques have been opportunistically employed to study the scattered presences of golden jackals (Canis aureus) in various localities of the Province of Verona (Veneto Region) and neighbouring surrounndings. The results so far indicate a rare scattered presence of the species, with at least one reproductive territorial group dwelling near Garda Lake, in Castelnuovo del Garda Municipality (Province of Verona). These first results have been then discussed within the knowledge about this rare wild dog in Italy, in order to correctly evaluate them from a protection, scientific and management point of view.
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The Authors refer about the first data on Canis aureus in northeastern Italy and northwestern. Istria.
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The paper update to 1992 some new data about Canis aureus in Italy, together with the first data about this species in Italy, referred to 1984.
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Broadcasted jackal howls were used to survey the status of the golden jackal in Greece. All sites with recent indication of jackal presence were surveyed at selected calling stations, and minimum population estimates were recorded. The results of the survey show that both populations and distribution area of the golden jackal in Greece have been declining steadily during the last three decades. The golden jackal has disappeared from Central and Western Greece and is currently confined in discontinuous, isolated population clusters in Peloponnese, Fokida, Samos isl., Halkidiki and North-eastern Greece. The reduction was more distinct in Southern Greece, which used to be the jackal's main area 20 years ago. The current minimum size of the jackal population in Greece was estimated at 152-162 different territorial groups. The largest population cluster was found in Nestos - Vistonida area, NE Greece. In Southern Greece, the jackal is found in the Mediterranean maquis zone at altitudes below 600m asl. Some individuals were observed up to 1000m asl, but were considered exceptional. In Northern Greece the species was found in areas below 250m asl, while the highest population densities were found in thickets around wetlands up to 10m asl.
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The article presents the record of an adult female golden jackal (Canis aureus) accidentally shot in 2005 near Gornji Grad in the Upper Savinja Valley, Northern Slovenia (UTM VM82, 980 m a.s.l.). Although this individual was most likely a vagrant, it indicates that golden jackals may soon, or perhaps already have, established permanent territories in Slovenia. Further studies are necessary to determine the status and distribution of this protected species in Slovenia, as well as public awareness actions, especially among hunters, in order to avoid additional accidents at hunting.
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Until 1920 Dalmatian jackals populated S Dalmatia and adjacent regions of the Montenegrin coast; at the beginning of the century they spread into N Dalmatia where they established a permanent population between 1920-1980 -Authors
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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.
Immigrazioni: ecco il primo sciacallo italiano
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Short note: First breeding record of the golden jackal (Canis aureus Linnaeus, 1758, Canidae) in Austria
HERZIG-STRASCHIL, B. (2008)-Short note: First breeding record of the golden jackal (Canis aureus Linnaeus, 1758, Canidae) in Austria. Ann. Naturhist. Mus. Wien, 109 B: 73-76.
Golden jackals (Canis aureus L.) on the Pelješac Peninsula (southern Dalmatia, Croatia
KROFEL M., 2007-Golden jackals (Canis aureus L.) on the Pelješac Peninsula (southern Dalmatia, Croatia. Natura Croatica, Zagreb, 16(3): 201-204.