Printer Friendly

Diet composition of the golden jackal and the sympatric red fox in an agricultural area (Hungary).

Abstract. In order to better understand the ecology of the golden jackal (Canis aureus) and interspecific relationships among carnivores, we studied its dietary pattern and the diet of its main competitor, the red fox (Vulpes vulpes) over a three-year period. The study was carried out in an agricultural area in SW Hungary and was based on scat analysis (jackal n = 373, fox n = 268 samples). The jackal primarily consumed small mammals in all seasons (mean biomass consumed: 72 %). The secondary food sources were wild ungulates (in winter and spring; mainly wild boar Sus scrofa, including piglets) and plants (in summer and autumn; mainly wild fruits). The consumption of cervids in winter and in spring was only detected in low proportions. The fox also primarily consumed small mammals (50.3 % of trophic niche breadth, B), but their consumption dropped in summer and autumn. Two-thirds of the summer and autumn diet consisted of plants, while the bird consumption was higher in spring and summer. The diet compositions of both predators were similar. However, compared with jackal, the fox consumed significantly higher proportions of birds. The standardized trophic niche breadth ([B.sub.A]) of these canids was very narrow (0.09), and the food overlapped in high proportions (69.8 %). The study confirmed the partial partitioning of food resources and opportunistic feeding of both canids.

Key words: Canis aureus, Vulpes vulpes, feeding ecology, trophic niche, opportunistic feeding, resource partitioning


The golden jackal (Canis aureus Linnaeus, 1758), a developed social system living mesocarnivore species, is spreading mainly in areas of Central and South-East Europe, including Hungary (Arnold et al. 2012). Its population size is continuously increasing (Szabo et al. 2009), and recently there has been an increase of reproductive populations in northern regions of Europe (Rutkowski et al. 2015). There are many common beliefs about the jackal, especially on its feeding habits (Szabo et al. 2010, Mihelic & Krofel 2012, Boskovic et al. 2013). The backgrounds of such beliefs are often unknown or can be easily misinterpreted lacking knowledge of real causes.

The golden jackal feeds upon a broad range of smaller sized prey, such as rodents, hares, birds, reptiles and arthropods (Demeter & Spassov 1993, Mukherjee et al. 2004, Lanszki et al. 2006, Jaeger et al. 2007), but also consumes plants (Demeter & Spassov 1993, Mukherjee et al. 2004, Aiyadurai & Jhala 2006, Borkowski et al. 2011), and scavenges on domestic animal remains (Macdonald 1979a, Poche et al. 1987, Lanszki et al. 2009, Giannatos et al. 2010, Lanszki et al. 2010, Borkowski et al. 2011, Boskovic et al. 2013, Penezic & Cirovic 2015), and different kinds of wild ungulate carcasses left by large predators (Aiyadurai & Jhala 2006) or hunters (Lanszki & Heltai 2002, Boskovic et al. 2013, Raichev et al. 2013, Lanszki et al. 2015). The group-living jackal successfully preys on medium- and larger-sized wild and domestic ungulates, especially fawns and calves (Demeter & Spassov 1993, Yom-Tov et al. 1995), or wounded, injured and weakened adults (Lanszki et al. 2006, 2015).

The red fox (Vulpes vulpes Linnaeus, 1758) is one of the most widespread and important mesopredators in the Northern Hemisphere (Macdonald & Sillero-Zubiri 2004). In agricultural areas the fox preys primarily on small mammals or hares, and periodically eats birds, carrion, plants and invertebrates (e.g. Englund 1965, Goszczynski 1977, Macdonald 1977, Jensen & Sequeira 1978, Goszczynski 1986, Jedrzejewska & Jedrzejewski 1998, Leckie et al. 1998, de Marinis & Asprea 2004). Due to the well known ecology as well as feeding habits of the red fox, it may represent a useful basis for comparison with less well studied competitors such as the jackal. The comparative dietary analyses can also facilitate exploring interspecific interactions (Lanszki et al. 2006). The red fox and the golden jackal are also considered to be generalist species for food and habitat (Macdonald & Sillero-Zubiri 2004). Because of the dramatic decline of large carnivore populations in Europe (Macdonald & Sillero-Zubiri 2004, Chapron et al. 2014), both have become top predators in a majority of the areas they occur in.

The differences between the golden jackal and the red fox arise for example from differing body mass (average of genders, jackal: 9.6-10.8 kg, fox: 5.4-6.3 kg; Heltai et al. 2010, Lanszki et al. 2015), body shape (jackal: longer legs, stronger toothing; Demeter & Spassov 1993, Heltai et al. 2010), activity period (jackal: arrhythmic, fox: nocturnal and crepuscular; Gittleman 1985, Heltai et al. 2010, Lanszki et al. 2015), and hunting techniques (Macdonald 1979b, Bekoff et al. 1984, Yom-Tov et al. 1995). Furthermore, the social system of the golden jackal, depending on the food resources is flexible (Macdonald 1979b, 1983). Although the cooperative hunting of jackals was only clearly proved in Africa (Kruuk 1972, Lamprecht 1978, Moehlman 1987) where they are separate Canis species (e.g. Rueness et al. 2011), the golden jackal can hunt not only solitary, but also in a pair, and in a smaller or larger family group with "helpers" and youngsters (Macdonald 1979b, 1983, Demeter & Spassov 1993). Cooperative hunting means competitive advantage compared to the solitary fox (Lloyd 1980) and could be related to habitat (Demeter & Spassov 1993). Larger and social carnivores (Bekoff et al. 1984, Gittleman 1985, 1989), such as the golden jackal, are more effective in preying on smaller or larger animals, because they can change the hunting techniques, while the smaller red fox preys on relatively smaller animals. Therefore, the jackal, unlike the fox, can be a pursuer hunter, not only a searcher hunter (Bekoff et al. 1984). The feeding habits besides prey size or abundance of food resources (e.g. Macdonald 1977, Jedrzejewska & Jedrzejewski 1998, Hungary: Lanszki et al. 2006, 2007), are influenced by numerous behavioural and ecological factors, e.g. zonation, habitat or environmental association of prey species (Gittleman 1985), which is less known in European carnivores. Therefore, in this study, behavioural and ecological features of consumed species are also compared between two sympatric canids.

Previous studies performed on agricultural areas in Hungary (periods examined: 1996-1997 and 2000-2004; Lanszki & Heltai 2002, Lanszki et al. 2006, Lanszki & Heltai 2010) showed similarity in diet composition and small mammal preference, trophic niche of both canids was narrow, but there were detectable characteristic differences as well. For example, more marked seasonal and inter-year differences were found in the diet composition of foxes than jackals, but area specific differences are less known. Better knowledge of intraspecific, interspecific and area related differences in diet compositions and feeding habits of these species may strengthen the biological basis of wildlife management.

Assuming, that the larger body massed, social predator takes larger prey more often than the smaller, solitary hunter (Bekoff et al. 1984, Gittleman 1985, 1989), the first prediction was, there should be considerable intraspecific differences in feeding habits, that is, the golden jackal should consume wild ungulates, meanwhile the red fox should consume small mammals in greater proportion. The second prediction was that the more varied diet jackal should be more food generalist than the fox. Based on the resource partitioning hypothesis (Hardin 1960, Rosenzweig 1966), the third prediction was that there should be a slight trophic niche overlap between the sympatric mesopredator species, because they use the resources (e.g. the prey species) in different ways, namely they partition it.

The aims of this three-year study performed in an agricultural area were 1) to evaluate the diet composition of the sympatric golden jackal and red fox, 2) to examine the trophic niche breadth and the intraspecific trophic niche overlap, 3) to investigate the feeding habits of canids based on the body mass, zonation, habitat association and environmental association of prey species in the diet, and 4) to examine the differences between the diet compositions of the golden jackal and the sympatric red fox in different areas based on Hungarian studies.

Material and Methods

Study area and study species

The study area is located in the Pannonian biogeographical region of SW Hungary (Vajszlo region, centre: 45[degrees]51' N, 17[degrees]56' E), plains area, close (6 km) to the River Drava. Although it is an inland water hazardous area, most of the land is used for arable agricultural cultivation. The vegetation consists of a mosaic of different habitat types, i.e. cultivated lands [59-60 %, mainly cereals, less extent watermelon (Citrullus lanatus), maiden grass (Miscanthus sinensis)], forests [29 %, mainly English oak (Quercus robur) and European hornbeam (Carpinus betulus), less extent poplar (Populus) and locust (Robinia)], and the 11-12 % of the total area is abandoned grasslands [partially covered by blackthorn (Prunus spinosa), common hawthorn (Crataegus monogyna), sedge (Carex)], common reed (Phragmites australis) and oxbow lakes covered by reed, bulrush (Typha), willow (Salix), alder (Alnus) and Canadian goldenrod (Solidago canadensis).

The study area lies on the continental climatic region, but there are some Mediterranean features (i.e. moderately warm and wet and relatively mild winter, Dovenyi 2010). During the study period the mean annual temperature was 10.9 [degrees]C (winter 0.5 [degrees]C, summer 17.5 [degrees]C). The annual number of days with snow cover was 14-21, with the average snow depth of 5 cm (20 cm in February 2012) and the mean annual precipitation was 862 mm (less than 500 mm in 2011 and above 1000 mm in 2010 and 2013).

Hunting bag data (individuals/[km.sup.2], mean [+ or -] standard error SE) between the 2010/11 and 2012/13 hunting years were as follows: red deer (Cervus elaphus) 1.92 [+ or -] 0.25, roe deer (Capreolus capreolus) 0.80 [+ or -] 0.09, wild boar (Sus scrofa) 3.69 [+ or -] 0.33 and pheasant (Phasianus colchicus) 0.59 [+ or -] 0.23 (Csanyi 2011, 2012, 2013, 2014). In the study area the big game management is less intensive than at some other game management units in SW Hungary (Lanszki et al. 2015).

The mean ([+ or -] SE) golden jackal density of the area was 0.35 [+ or -] 0.08 group/[km.sup.2] plus 0.11 [+ or -] 0.01 individuals/[km.sup.2], calculated from records of five surveys between November 2010 and March 2013 by the stimulated calling method (Giannatos et al. 2005). The hunting bag density of the golden jackal between 2010 and 2013 was 0.28 [+ or -] 0.11 individuals/[km.sup.2], while that of the red fox was 0.24 [+ or -] 0.16 individuals/[km.sup.2]. The area was also inhabited by several other predators, including the Eurasian badger (Meles meles), stone marten (Martes foina), pine marten (Martes martes), Eurasian otter (Lutra lutra) and white-tailed eagle (Heliaeetus albicilla). There was no grazing in the study area.

Scat collection and diet analysis

The diet composition and feeding habits of the golden jackal and the red fox were investigated by analysis of scats collected two times per season from July 2010 to May 2013. Scat samples (each corresponding to one scat and not to a pile, Macdonald 1979a) were collected on a 13.6 km long standard route within a 6.1 [km.sup.2] area, through agricultural land. Samples were frozen at -20 [degrees]C for three months prior to analysis. Jackal and fox scat samples were distinguished on the basis of odour, size and shape characteristics (Macdonald 1980). Stray dogs were very rare or not present in the area. Questionable samples (1-2 %) were not collected or excluded from the analysis.

A total of 373 golden jackal and 268 red fox scats were analyzed by means of a standard procedure (Jedrzejewska & Jedrzejewski 1998). Scats were soaked in water, then washed through a sieve (0.5 mm mesh) and finally dried. All food remains were separated, and using a microscope, all feather, bone, dentition, and hair specimens identified using keys from Marz (1972), Teerink (1991), Brown et al. (1993), and our own vertebrate, invertebrate and plant reference collections. Diet composition of the predators was expressed in two ways (Tables 1 and 3): relative frequency of occurrence (%O, number of occurrences of a certain food type divided by the total number of food occurrences of all food types and then multiplied by 100), and percentage of biomass consumed (%B). To estimate the fresh mass of food ingested (Reynolds & Aebischer 1991), all dry food remains were weighed separately (measured at the 0.01 g accuracy) and the food remain mass was multiplied by an appropriate conversion factor (i.e. coefficient of digestibility), as summarized from literature data by Jedrzejewska & Jedrzejewski (1998) for red fox (i.e. insectivores and small rodents x 23, medium sized mammals x 50, wild boar x 118, deer x 15, birds x 35, reptiles x 18, fish x 25, insects and molluscs x 5, fruit, seed and other plant material x 14, for both mesocarnivores). For wild boar and cervids we used various coefficients of digestibility, suggested by Jedrzejewski & Jedrzejewska (1992) and applied in other studies (e.g. Lanszki et al. 2006, 2010). Non-food (generally indigestible) substances ingested were not included in the calculation.

Recorded animal food types were classified according to body mass and behavioural or ecological variables (Gittleman 1985, Clevenger 1993, Lanszki et al. 2006, 2007, 2010). Firstly, prey species were classified on the basis of their mass (< 15 g, 15-50 g, 51-100 g, 101-300 g, 301-1000 g, and > 1000 g). The second classification was based on the "zonations" (behavioural feature) such as: terrestrial (and mainly terrestrial but sometimes arboreal); arboreal (and mainly arboreal but sometimes terrestrial); and aquatic (or water-related). Thirdly, they were classified on the basis of their typical habitat associations (or vegetation). Classes were: open field species (e.g. common vole Microtus arvalis); forest species or species living in dense shrubbery (e.g. bank vole Myodes glareolus); and habitat generalist species which may live both in open fields and in forests (e.g. Apodemus mice, European brown hare Lepus europaeus, wild ungulates). Fourthly, animal food species were classified on the basis of their typical environmental associations, such as: human-linked, wild, and mixed (which may live both near settlements and in the wild).

The following 11 food categories were used in the calculations related to the comparative analysis of the scat composition and the trophic niche for predator species: 1--small mammals (insectivores and rodents), 2--European brown hare, 3--wild carnivores, 4--wild boar, 5--cervids, 6--pheasant, 7--other birds, 8--reptiles and amphibians, 9--invertebrates, 10--domestic animals and 11--fruits, seeds and other plant matter.

Data analysis

General log-linear likelihood tests were used on frequency of occurrence data to test for interspecific (between golden jackal and red fox) and intraspecific differences of two carnivore species for four seasons and three years. The unit of analysis was jackal and fox scats and the response variable was the presence or absence of the food item considered. The model was fitted using carnivore species, season and year as independent variables. Owing to the large number of comparison (11 food categories), we adjusted the level of significance to 0.0045 with a Bonferroni correction. The consumption of 11 food categories on the basis of the estimated percentage of biomass consumed (arcsin transformed %B values) was also compared between the two predators using paired samples t-test. Multivariate analysis of variance (MANOVA, Bonferroni post-hoc test, GLM procedure) was applied to explore intraspecific differences in consumption of fresh biomass of preys (arcsin transformed %B for both canids as dependent variables, season and year as fixed factors and weighed by food types).

Trophic niche breadth was calculated in accordance with Levins (Krebs 1989): B = 1/[SIGMA] [p.sub.i.sup.2], where pi is the relative frequency of occurrence or the percentage biomass proportion of the ith food item; and standardised across food items: [B.sub.A] = (B - 1)/(n - 1), rating from 0 to 1. The trophic niche overlap was calculated by the Renkonen index (Krebs 1989): [P.sub.jk] = [[SIGMA]n(minimum [p.sub.ij], [p.sub.ik])]100, where [P.sub.jk] is the percentage overlap between species j and species k; [p.sub.ij] and [p.sub.ik] are the proportion of the resource i which is represented within the total resources used by species j and species k (the minimum means that the smaller value should be used); n is the total number of the resource taxa (of the 11 categories listed above). The standardised trophic niche breadth values were compared with paired samples t-test. The consumption of animal food according to body mass and three behavioural or ecological features (zonation, habitat and environmental association) on the basis of percentage relative frequency of occurrence (%O) and estimated biomass (%B) values were compared using G-test.

Hierarchical cluster analysis (cluster method: between-groups linkage, interval of measure: Euclidean distance ranged between 0 and 100) was applied to compare diet composition among golden jackals and red foxes from different study sites in Hungary (Lanszki & Heltai 2002, Lanszki et al. 2006, 2015), including this study. Dendrogram was performed on the basis of arcsin transformed percentage relative frequency (%O) and consumed biomass (%B) data of 10 main food types (same food types as listed above, except pheasant and other birds were merged). The SPSS 10.0 for Windows (1999) and R (v. 3.2.3., R Development Core Team, Vienna, Austria) statistical package were used for data processing.


Golden jackal diet

Small mammals were dominant in the diet of the golden jackal (annual mean, %O: 65.1 %, %B: 72.0 %, Table 1). Proportion of small mammal consumption ranged between 28.6 and 79.7 % (%O) or 36.1 and 95.8 % (%B) among seasons and years (Fig. 1) in the scat samples. The main prey was the common vole. Besides the common vole, important prey species were also field mice (Apodemus sp.), bank vole and European water vole (Arvicola amphibius). Carnivores (Eurasian badger, domestic cat) occurred rarely in the diet; European brown hares were eaten in small amounts. Wild ungulates were the second most important (%B) or third food type (%O, Table 1). The most important ungulate species was the wild boar (piglets in the spring and summer), consumption of which greatly fluctuated among seasons and years (Fig. 1). The presence of cervids in the samples was low (Table 1). Other vertebrates, such as birds, lizards, snakes, frogs, and invertebrates (mainly beetles) were consumed in low quantitative proportions. Depending on season jackals supplemented their diet mainly with wild fruits and corn (Table 1). In the analyzed samples inorganic materials (i.e. plastic, rag, gravel and paper) occurred very rarely (in 1-1 case).

Food item occurrence in the diet of golden jackal based on scat analysis showed only occasional significant differences (i.e. invertebrates, plants) among seasons (log-linear analysis, Table 2), while season x year interactions were significant in all food types. No significant differences were found in consumption ratios (%B) depending on season (MANOVA, [F.sub.3] = 0.30, P = 0.825), year ([F.sub.2] = 0.20, P = 0.817) or their interactions ([F.sub.5] = 0.32, P = 0.901). In the jackal diet, the role of small mammals was significant in all seasons, their consumption increasing from spring (%O: 55.1 %, %B: 61.9 %) or summer (%O: 44.6 %, %B: 63.0 %) to winter (%O: 77.2 %, %B: 78.2 %). The ungulates and the plants switched places with each other in the diet. The jackal consumed ungulates in spring and winter, while plants in summer and autumn in higher proportions.

Red fox diet

Small mammals were also the primary food type of the red fox (annual mean, %O: 41.9 %, %B: 50.3 %, Table 3) in the scat samples. Their consumption fluctuated between 13.4 and 73.0 % (%O) or 16.9 and 87.1 % (%B) among seasons and years (Fig. 1). Most important prey species were the Microtus voles (mainly common vole). In addition, important prey species were field mice and water vole. The brown hare occurred very rarely in fox scat samples but its consumption was occasionally (in spring 2011) relatively high (Fig. 1). Almost one third of the diet consisted of plants, these (especially the wild fruits) were a secondary important food item in the fox diet (Table 3). The consumption of plants showed great inter-year differences and varied over a wide range (Fig. 1). Third most important items of the fox were ungulates; the most important species was the wild boar (mainly piglets). The wild boar consumption largely fluctuated during the study period (most in 3013; Fig. 1), while cervids were eaten in small amounts. The bird (mainly medium-sized species) consumption was considerable in spring and summer (Fig. 1). Other vertebrates, such as carnivores, lizards, snakes, snake eggs, and invertebrates were consumed in small amounts. The analyzed scat samples contained inorganic materials (i.e. pieces of plastic, gravel, textile and cigarette butts) very rarely (in 1-1 case).

The diet composition of the red fox showed occasional significant differences (i.e. small mammals, invertebrates, plants) among seasons (log-linear analysis, Table 2), the difference among years was significant only in case of the wild boar, season x year interactions were significant in all food types. No significant differences were found in consumption ratios (%B) depending on season (MANOVA, [F.sub.3] = 0.42, P = 0.741), year ([F.sub.2] = 0.47, P = 0.622) or these interactions ([F.sub.4] = 0.49, P = 0.740). In winter and spring the consumption of small mammals was (%O: 48.4-57.3 %, %B: 63.1-64.9 %), and it significant dropped in summer (%O: 20.2 %, %B: 23.8 %) and autumn (%B: 32.8 %, %O: 32.4 %), while consumption of plants increased (%O: 42.3-57.4 %, %B: 65.7-66.8 %). Interspecific differences in dietary composition and trophic niche

Main effects of carnivore species (log-linear analysis, Bonferroni test) were significant in the consumption of "other birds" (all birds without pheasant; [[chi square].sub.1] = 9.52, P = 0.0020) or summarized data of birds (all birds, including pheasant; [[chi square].sub.1] = 8.17, P = 0.0043). Compared with 6 jackal, the fox consumed more frequently birds. Main effects of season were significant in the consumption of small mammals ([[chi square].sub.3] = 18.28, P = 0.0004) and summarized data of reptiles and amphibians ([[chi square].sub.3] = 16.67, P = 0.0008), and main effect of year was significant only in the consumption of wild boar ([[chi square].sub.2] = 12.53, P = 0.0019), interactions were not significant. Compared with jackal, the fox consumed significantly higher proportions (%B) of "other birds" (paired samples t-test, [t.sub.9] = 3.39, P = 0.008) and invertebrates ([t.sub.9] = 2.59, P = 0.029).

Jackal and fox scat samples contained 33 and 32 different animal taxa (i.e. species or higher taxa), as well as 13-13 plant taxa, respectively. The standardized trophic niche ([B.sub.A], Table 1 and 3) of both predators was equally narrow (paired samples t-test, occurrences: [t.sub.9] = 2.01, P = 0.075, biomass data: [t.sub.9] = 2.01, P = 0.884) and the mean ([+ or -] SE) trophic niche overlap value was high (biomass data: 69.8 [+ or -] 5.27 %, occurrences: 73.8 [+ or -] 2.77 %).

Small-sized, terrestrial, open field living or habitat generalist and wild living animals were the most important food for both predators (Table 4). Significant interspecific differences were found (Table 4) in consumption of 301-1000 g prey category (for %O data), in arboreal, open- and forest-living species and animals which may live both near settlements and in the wild. In general, jackal, consumed higher ratios of forest-living and lower ratios arboreal species than fox.

Area specific differences in diet compositions

On the basis of Euclidean distances ([E.sub.d]) from the hierarchical cluster analysis (Fig. 2), the mean dissimilarity among overall diet compositions of jackal and fox from different studies from Hungary was 32.9 (%O data) and 41.1 (%B data). Mean [E.sub.d] among all group pairs ranged between 9.9 and 58.1 (%O data) or between 13.2 and 80.5 (%B data). Independently of variable (%O or %B) jackal and fox from Vajszlo and Ketujfalu, as they mainly consumed small mammals (Fig. 2), fell into one group and Labod, where jackals consumed mainly viscera and carrion of wild ungulates, fell into another group. On Mike-Csokoly area, jackals and foxes consumed wild ungulates (mainly from carrion) and small mammals as primary foods, so they fell into the third cluster for %B data, while foxes, due to frequent bird consumption fell into a separated group for %O data in the cluster analysis.


The feeding habits of the golden jackal and the red fox in the studied agricultural area showed similarity in that their primary food was small mammals, and they consumed other food types in high proportions periodically. Therefore, the first prediction was partially supported by the differences found in dietary patterns. The diet of jackal was characterized by the dominance of small mammals in all seasons; the secondary food types were ungulates during winter and spring, and plants during summer and autumn.

The seasonal and inter-year variation of the diet composition was high in this study similarly as in the Balkans (Radovic & Kovacic 2010, Markov & Lanszki 2012, Boskovic et al. 2013, Penezic & Cirovic 2015), and it was higher than in a nearby (distance around 20 km) agricultural area, where abandoned fields were at a greater extent (Ketujfalu region, Lanszki et al. 2006). The fox dietary pattern showed greater differences among seasons than that of the jackal. Consumption of plants periodically exceeded (in summer and autumn) the small mammal consumption, however, other items, like ungulates (in winter and spring) and birds (in spring and summer) were considerable food sources too. The seasonal variation in fox diets was higher than in an earlier study in this region (Lanszki et al. 2006), and in research carried out in other agricultural areas (Lever 1959, Jensen & Sequeira 1978, Goszczynski 1986, Lanszki et al. 1999, Goldyn et al. 2003), seasonal and inter-year differences in fox diets were found to be just great.

Contrary to our expectations, the larger sized jackal consumed small mammals in higher proportion; despite the biologically important difference, it was supported statistically only for relative frequency (%O) calculation. Small mammal dominated diets are known mainly from agricultural areas where both the jackal (Khan & Beg 1986, Lanszki et al. 2006, Jaeger et al. 2007) and the fox occur (Englund 1965, Jensen & Sequeira 1978, Lanszki et al. 1999), however exceptions are also known (e.g. Lever 1959, Kozena 1988, Goldyn et al. 2003). The most important food was the agricultural pest, the common vole for both canids.

As we expected, interspecific difference in consumption of wild ungulates was significant. However, consumption ratio of ungulates was lower than experienced in other studies in southern areas (Demeter & Spassov 1993, Radovic & Kovacic 2010, Boskovic et al. 2013) and in intensively managed big game areas (Lanszki et al. 2015), or common beliefs (summary: Szabo et al. 2010). Within ungulates, for the golden jackal, the periodically important (secondary or buffer) food was the wild boar, while the cervids consumption was occasional. In studies where considerable ungulate consumption were found, golden jackals (Aiyadurai & Jhala 2006) or similar, medium-sized Canis species (Moehlman 1987), consumed prey remains of larger predators or eat carrion, which were usually remains left from official hunting or poaching (Lanszki & Heltai 2002, Radovic & Kovacic 2010, Boskovic et al. 2013, Lanszki et al. 2015, Penezic & Cirovic 2015), or the predation happened in a fenced area (Prerna et al. 2015). Although, the consumption of cattle calves (Yom-Tov et al. 1995) is known on open grass lands.

Regarding golden jackals, in addition to solitary hunting and scavenging (Macdonald 1983, Demeter & Spassov 1993), co-operative hunting probably also occurred on wild boar piglets or wounded ungulates. Due to limitations of the applied methodology (Reynolds & Aebischer 1991), it is not exactly known what proportion of wild boars or cervids were directly preyed on by predators, and what proportion was carrion. Carcasses (from natural mortality, sport hunting, road kill, poaching) and remains (e.g. viscera left by hunters) of wild ungulates are available in high quantity for predators in SW Hungary (Lanszki et al. 2015). Jackals might remove injured or dead ungulates within a night (Lanszki et al. 2006), and in these cases insect larvae in the scats cannot indicate the real scavenging activity. Because of these, in the case of the jackal, occasional occurrence of direct predation and predominance of scavenging indicates that the solitary red fox also consumed ungulates periodically in relatively high proportions, although the occurrence of direct predation could not be excluded for the foxes, either. Considerable periodical ungulate consumption (partially from scavenging) of the fox was shown in other European studies (e.g. Englund 1965, Fedriani & Traviani 2000, Baltrunaite 2002, Lanszki & Heltai 2002, Cagnacci et al. 2003, Lanszki et al. 2006, 2007).

Plants were the secondary (buffer) food for the golden jackals, while for the red fox they were temporarily the primary food source. In this food item, both canids consumed the seasonally ripening wild fruits (plum, blackthorn, cherry, pear) and corn. Although for the jackal, the plants consumption was periodically high in this study, in total, it was lower than that recorded in warmer climate areas (Mukherjee et al. 2004, Aiyadurai & Jhala 2006), however, it was higher than in an earlier study in this region (Lanszki et al. 2006). Feeding temporarily based on plants, can help the omnivorous predator to survive in critical periods (Poche et al. 1987, Mukherjee et al. 2004), however also indicates competitive disadvantages, as in the case of the sympatric fox and jackal have experienced (Lanszki et al. 2006).

The bird consumption of both canids was similar to an earlier study performed in this region (Lanszki et al. 2006), and was lower than in other areas where birds are more abundant (golden jackal: Demeter & Spassov 1993, Lanszki et al. 2009, red fox: Lever 1959, Kolb & Hewson 1979, Goldyn et al. 2003, Lanszki et al. 2007). The bird consumption of the fox was substantially higher during nesting period. The differences in bird consumption found also indicate interspecific differences between the species.

Consumption of other food items was occasional. No predation on livestock, only consumptions of domestic cat and dog were detected in the golden jackal and the red fox scat samples. Studies on the feeding habits of the golden jackal across its geographical range indicate that domestic animals (poultry, ungulates, dog) are important food items especially in south-east Europe and Israel (Macdonald 1979a, Yom-Tov et al. 1995, Lanszki et al. 2009, Giannatos et al. 2010, Lanszki et al. 2010, Radovic & Kovacic 2010, Boskovic et al. 2013, Penezic & Cirovic 2015), but in these cases the carrion eating was dominant, as in the case of the fox in other studies (Englund 1965, Jensen & Sequeira 1978, Baltrunaite 2002, Cagnacci et al. 2003). In this study the detected domestic animal consumption was lower than in an earlier study in this region (Lanszki et al. 2006) which has likely arisen from lack of used nearby garbage dumps (Bino et al. 2010). The low brown hare consumption could depend mainly on the low hare density in this region (Csanyi et al. 2014). Both predators consumed reptiles and amphibians rarely, arthropod frequently, but in low quantitative ratios. The second prediction was not supported because the trophic niche of both canids was similarly very narrow in this study, as in case of food specialist species (Hanski et al. 1991). However, in the case of generalist species (Kruuk 1989, Jedrzejewska & Jedrzejewski 1998), the diet of both canids was diverse, and feeding habits were flexible (Macdonald 1979a, Demeter & Spassov 1993, de Marinis & Asprea 2004), utilizing the seasonally available food resources. The third prediction was only partially supported. Due to similarities in diet compositions, the trophic niche overlap between the two predators was high. These results (diverse diet, opportunistic feeding, narrow trophic niche, high trophic niche overlap) are consistent with earlier studies carried out in Hungary (Lanszki & Heltai 2002, Lanszki et al. 2006). Despite high trophic niche overlap values, these two canids can undertake long term coexistence, which is supported by the national game management data (Szabo et al. 2009, Csanyi et al. 2014). One of the most important reasons for this can be that they utilise many resource in varying degree at the same time.

According to the body mass and ecological features of consumed animals, the niche of the two canids differed, which confirmed partially our third prediction (food partitioning). However both canids consumed mainly small-sized, terrestrial, open field living and wild animals, but the jackal, compared to the fox, consumed a lower proportion of arboreal and higher proportions of forest and wild living species.

The hierarchical cluster analysis of diet composition of golden jackals and red foxes from different studies from Hungary identified three groups. Wild ungulate (carrion) consumption increased, while small mammal consumption decreased along a gradient with increasing forest coverage and intensity of big game management, i.e. from agricultural areas as Vajszlo (forest coverage 29 %, present study area) and Ketujfalu (forest coverage 26 %, Lanszki et al. 2006), through Mike-Csokoly (forest coverage 39 %, Lanszki & Heltai 2002) to Labod (forest coverage 52 %, Lanszki et al. 2015) in case of both canids. Based on these studies, the diet compositions differed to a greater extent depending on the area (habitat type and/or wildlife management) rather than depending on the species (jackal or fox).

In conclusion, better knowledge of the ecological role of mesocarnivores, i.e. the spreading golden jackal and the most common wild canid, the red fox in food webs, may facilitate the choice of appropriate management approaches. Further field studies need to explore community level and area specific trophic interactions especially in human dominated habitats. The experienced temporary dietary specialization and the long-term generalization show high feeding flexibility of both canids. This is beneficial for the golden jackal to occupy new territories across Europe, and for the red fox to coexist with the jackal, as a larger-sized competitor.


Thanks to Laszlo Torbo for his assistance during field works and anonymous reviewers for helpful advice and comments. This study was supported by the Bolyai Scholarship (JL), Hungarian-Serbian bilateral programme (project no.: RS-14/09) and the "Research Faculty Grant" of the "Hungarian Ministry of Human Resources" (registration no.: 7629-24/2013/TUDPOL; MH, LSZ).


Aiyadurai A. & Jhala Y.V. 2006: Foraging and habitat use by golden jackals (Canis aureus) in the Bhal region, Gujarat, India. J. Bombay Nat. Hist. Soc. 103: 1-10.

Arnold J., Humer A., Heltai M. et al. 2012: Current status and distribution of golden jackals Canis aureus in Europe. Mammal Rev. 42: 1-11.

Baltrunaite L. 2002: Diet composition of the red fox (Vulpes vulpes L.), pine marten (Martes martes L.) and raccoon dog (Nyctereutes procyonoides Gray) in clay plain landscape, Lithuania. Acta Zool. Lit. 12: 362-368.

Bekoff M., Daniels T. & Gittleman J.L. 1984: Life history patterns and the comparative social ecology of carnivores. Annu. Rev. Ecol. Syst. 15: 191-232.

Bino G., Dolev A., Yosha D. et al. 2010: Abrupt spatial and numerical responses of overabundant foxes to a reduction in anthropogenic resources. J. Appl. Ecol. 47: 1262-1271.

Borkowski J., Zalewski A. & Manor R. 2011: Diet composition of golden jackals in Israel. Ann. Zool. Fenn. 48: 108-118.

Boskovic I., Speranda M., Florijancic T. et al. 2013: Dietary habits of the golden jackal (Canis aureus L.) in the Eastern Croatia. Agric. Conspec. Sci. 78: 245-248.

Brown R., Ferguson J., Lawrence M. & Lees D. 1993: Federn, Spuren und Zeichen der Vogel Europas: Ein Feldfuhrer. Aula-Verlag, Wiesbaden.

Cagnacci F., Lovari S. & Meriggi A. 2003: Carrion dependence and food habits of the red fox in an Alpine area. Ital. J. Zool. 70: 31-38.

Chapron G., Kaczensky P., Linnell J.D.C. et al. 2014: Recovery of large carnivores in Europe's modern human-dominated landscapes. Science 346: 1517-1519.

Clevenger A.P. 1993: Pine marten (Martes martes Linne, 1758) comparative feeding ecology in an island and mainland population of Spain. Z. Saugetierkd. 58: 212-224.

Csanyi S., Lehoczki R. & Sonkoly K. 2011: Hungarian game management database: 2010/2011 hunting year. Szent Istvan University, Godollo. (in Hungarian)

Csanyi S., Sonkoly K. & Lehoczki R. 2012: Hungarian game management database: 2011/2012 hunting year. Szent Istvan University, Godollo. (in Hungarian)

Csanyi S., Toth K., Kovacs I. & Schally G. 2014: Hungarian game management database: 2013/2014 hunting year. Szent Istvan University, Godollo. (in Hungarian)

Csanyi S., Toth K. & Schally G. 2013: Hungarian game management database: 2012/2013 hunting year. Szent Istvan University, Godollo. (in Hungarian)

de Marinis A.M. & Asprea A. 2004: The diet of red fox Vulpes vulpes and badger Meles meles in the Mediterranean ecosystems. Proceedings of the 10th MEDECOS Conference, Rhodes, Greece 1: 1-10.

Demeter A. & Spassov N. 1993: Canis aureus Linnaeus, 1758--Schakal, Goldschakal. In: Niethammer J. & Krapp, F. (eds.), Handbuch der Saugetiere Europas. Aula-Verlag, Wiesbaden: 107-138.

Dovenyi Z. 2010: Inventory of micro regions in Hungary. MTA Geographical Research Institute, Budapest. (in Hungarian)

Englund J. 1965: Studies on food ecology of the red fox (Vulpes vulpes) in Sweden. Viltrevy 3: 371-442.

Fedriani J.M. & Traviani A. 2000: Predator trophic guild assignment: the importance of the method of diet quantification. Rev. Ecol. Terre Vie 55: 129-139.

Giannatos G., Karypidou A., Legakis A. & Polymeni R. 2010: Golden jackal (Canis aureus L.) diet in Southern Greece. Mamm. Biol. 75: 227-232.

Giannatos G., Marinos Y., Maragou P. & Catsadorakis G. 2005: The status of the golden jackal (Canis aureus L.) in Greece. Belg. J. Zool. 135: 145-149.

Gittleman J.L. 1985: Carnivore body size: ecological and taxonomic correlates. Oecologia 67: 540-554.

Gittleman J.L. 1989: Carnivore group living: comparative trends. In: Gittleman J.L. (ed.), Carnivore behavior, ecology, and evolution. Cornell University Press, New York: 183-207.

Goldyn B., Hromada M., Surmacki A. & Tryjanowski P. 2003: Habitat use and diet of the red fox Vulpes vulpes in an agricultural landscape in Poland. Z. Jagdwiss. 49: 191-200.

Goszczynski J. 1977: Connections between predatory birds and mammals and their prey. Acta Theriol. 22: 399-430.

Goszczynski J. 1986: Diet of foxes and martens in central Poland. Acta Theriol. 31: 491-506.

Hanski I., Hansson L. & Henttonen H. 1991: Specialist predators, generalist predators, and the microtine rodent cycle. J. Anim. Ecol. 60: 353-367.

Hardin G. 1960: The competitive exclusion principle. Science 131: 1292-1297.

Heltai M., Lanszki J., Szemethy L. & Toth M. (eds.) 2010: Mammal predators in Hungary. Mezogazda Press, Budapest. (in Hungarian)

Jaeger M.M., Haque E., Sultana P. & Bruggers R.L. 2007: Daytime cover, diet and space-use of golden jackals (Canis aureus) in agroecosystems of Bangladesh. Mammalia 71: 1-10.

Jedrzejewska B. & Jedrzejewski W. 1998: Predation in vertebrate communities. The Bialowieza Primeval Forest as a case study. Springer-Verlag, Berlin.

Jedrzejewski W. & Jedrzejewska B. 1992: Foraging and diet of the red fox Vulpes vulpes in relation to variable food resources in Bialowieza National Park, Poland. Ecography 15: 212-220.

Jensen B. & Sequeira D.M. 1978: The diet of the red fox (Vulpes vulpes L.) in Denmark. Dan. Rev. Game Biol. 10: 1-16.

Khan A.A. & Beg M.A. 1986: Food of some mammalian predators in the cultivated area of Punjab. Pakistan J. Zool. 18: 71-79.

Kolb H.H. & Hewson R. 1979: Variation in the diet of foxes in Scotland. Acta Theriol. 24: 69-83.

Kozena I. 1988: Diet of the red fox (Vulpes vulpes) in agrocoenoses in southern Moravia. Acta Sc. Nat. Brno 22 (7): 1-24.

Krebs C.J. 1989: Ecological methodology. Harper Collins Publishers, New York.

Kruuk H. 1972: The spotted hyena. University of Chicago Press, Chicago.

Kruuk H. 1989: The social badger. Ecology and behaviour of a group-living carnivore (Meles meles). Oxford University Press, Oxford.

Lamprecht J. 1978: On diet, foraging behaviour and interspecific food competition of jackals in the Serengeti National Park, East Africa. Z. Saugetierkd. 43: 210-223.

Lanszki J., Giannatos G., Dolev A. et al. 2010: Late autumn trophic flexibility of the golden jackal (Canis aureus). Acta Theriol. 55: 361-370.

Lanszki J., Giannatos G., Heltai M. & Legakis A. 2009: Diet composition of golden jackals during cub-rearing season in Mediterranean marshland, in Greece. Mamm. Biol. 74: 72-75.

Lanszki J. & Heltai M. 2002: Feeding habits of golden jackal and red fox in south-western Hungary during winter and spring. Z. Saugetierkd. 67: 128-136.

Lanszki J. & Heltai M. 2010: Food preferences of golden jackals and sympatric red foxes in European temperate climate agricultural area (Hungary). Mammalia 74: 267-273.

Lanszki J., Heltai M. & Szabo L. 2006: Feeding habits and trophic niche overlap between sympatric golden jackal (Canis aureus) and red fox (Vulpes vulpes) in the Pannonian ecoregion (Hungary). Can. J. Zool. 84: 1647-1656.

Lanszki J., Kormendi S., Hancz Cs. & Zalewski A. 1999: Feeding habits and trophic niche overlap in a Carnivora community of Hungary. Acta Theriol. 44: 127-136.

Lanszki J., Kurys A., Heltai M. et al. 2015: Diet composition of the golden jackal in an area of intensive big game management. Ann. Zool. Fenn. 52: 243-255.

Lanszki J., Zalewski A. & Horvath Gy. 2007: Comparison of red fox and pine marten food habits in a deciduous forest. Wildlife Biol. 13: 258-271.

Leckie F.M., Thirgood S.J., May R. & Redpath S.M. 1998: Variation in the diet of red foxes on Scottish moorland in relation to prey abundance. Ecography 21: 599-604.

Lever J.A.W. 1959: The diet of the fox since myxomatosis. J. Anim. Ecol. 28: 359-375.

Lloyd H.G. 1980: The red fox. B.T. Batsford Ltd., London.

Macdonald D.W. 1977: On food preference in the red fox. Mammal Rev. 7: 7-23.

Macdonald D.W. 1979a: The flexible social system of the golden jackal, Canis aureus. Behav. Ecol. Sociobiol. 5: 17-38.

Macdonald D.W. 1979b: 'Helpers' in fox society. Nature 282: 69-71.

Macdonald D.W. 1980: Patterns of scent marking with urine and faeces amongst carnivore communities. Symp. Zool. Soc. Lond. 45: 107-139.

Macdonald D.W. 1983: The ecology of carnivore social behaviour. Nature 301: 379-383.

Macdonald D.W. & Sillero-Zubiri C. 2004: Biology and conservation of wild canids. Oxford University Press, Oxford.

Markov G. & Lanszki J. 2012: Diet composition of the golden jackal, Canis aureus in an agricultural environment. Folia Zool. 61: 44-48.

Marz R. 1972: Gewoll- und Rupfungskunde. Akademie Verlag, Berlin.

Mihelic M. & Krofel M. 2012: New records of the golden jackal (Canis aureus L.) in the upper Soca valley, Slovenia. Natura Sloveniae 14: 51-63.

Moehlman P.D. 1987: Social organization in jackals. Am. Sci. 75: 366-375.

Mukherjee S., Goyal S.P., Johnsingh A.J.T. & Pitman M.R.P. 2004: The importance of rodents in the diet of jungle cat (Felis chaus), caracal (Caracal caracal) and golden jackal (Canis aureus) in Sariska Tiger Reserve, Rajasthan, India. J. Zool. Lond. 262: 405-411.

Penezic A. & Cirovic D. 2015: Seasonal variation in diet of the golden jackal (Canis aureus) in Serbia. Mammal Res. 60: 309-317.

Poche R.M., Evans S.J., Sultana P. et al. 1987: Notes on the golden jackal (Canis aureus) in Bangladesh. Mammalia 51: 259-270.

Prerna S., Edgaonkar A. & Dubey Y. 2015: Status of golden jackal Canis aureus and ungulates in a small enclosed area--Van Vihar National Park, Madhya Pradesh, India. J. Threat. Taxa 7: 7416-7421.

Radovic A. & Kovacic D. 2010: Diet composition of the golden jackal (Canis aureus L.) on the Peljesac Peninsula, Dalmatia, Croatia. Period. Biol. 112: 219-224.

Raichev E.G., Tsonuda H., Newman C. et al. 2013: The reliance of the golden jackal (Canis aureus) on anthropogenic foods in winter in Central Bulgaria. Mamm. Study 38: 19-27.

Reynolds J.C. & Aebischer N.J. 1991: Comparison and quantification of carnivore diet by faecal analysis: a critique, with recommendations, based on a study of the fox Vulpes vulpes. Mammal Rev. 21: 97-122.

Rosenzweig M.L. 1966: Community structure in sympatric Carnivora. J. Mammal. 47: 602-612.

Rueness E.K., Asmyhr M.G., Sillero-Zubiri C. et al. 2011: The cryptic African wolf: Canis aureus lupaster is not a golden jackal and is not endemic to Egypt. PLoS ONE 6: e16385.

Rutkowski R., Krofel M., Giannatos G. et al. 2015: A European concern? Genetic structure and expansion of golden jackals (Canis aureus) in Europe and the Caucasus. PLoS ONE 10: e0141236.

Szabo L., Heltai M. & Lanszki J. 2010: Jackal versus livestock--is it a real problem? Hungarian Agricultural Research 19: 4-10.

Szabo L., Heltai M., Szucs E. et al. 2009: Expansion range of the golden jackal in Hungary between 1997 and 2006. Mammalia 73: 307-311.

Teerink B.J. 1991: Hair of West-European mammals. Cambridge University Press, Cambridge.

Yom-Tov Y., Ashkenazi S. & Viner O. 1995: Cattle predation by the golden jackal Canis aureus in the Golan Heights, Israel. Biol. Conserv. 73: 19-22.

Jozsef LANSZKI (1)*, Anita KURYS (1), Laszlo SZABO (2), Nikolett NAGYAPATI (1), Laura B. PORTER (3) and Miklos HELTAI (2)

(1) Kaposvar University, Carnivore Ecology Research Group, P.O. Box 16, 7401 Kaposvar, Hungary; e-mail:

(2) Szent Istvan University, Institute for Wildlife Conservation, Pater Karoly Str. 1, 2100 Godollo, Hungary

(3) Bangor University, College of Natural Sciences, Gwynedd, LL57 2DG Bangor, United Kingdom

* Corresponding Author

Received 11 February 2016; Accepted 2 December 2016

Table 1. Seasonal and annual relative frequency of occurrence and
biomass percentage of food items in scats of golden jackals (Canis
aureus) in Vajszlo, Hungary. Scat samples collected between July 2010
and May 2013, %O--relative frequency of occurrence, %B--percentage of
consumed biomass, + - biomass under 0.05 %, [B.sub.A]--standardized
trophic niche breadth value.

Food items                                Spring        Summer
                                          %O     %B     %O     %B

Microtus sp.                               27.1  30.4   16.9   25.8
Bank vole (Myodes glareolus)                7.7   8.0    3.1    6.1
European water vole (Arvicola amphibius)    4.8   8.8
Apodemus sp.                               10.6   9.8   15.4   21.5
Other small rodents                         1.9   1.1    3.1    2.6
Shrews (Soricidae)                          0.5   1.0    1.5    1.2
European mole (Talpa europaea)              2.4   2.7    4.6    5.8
European brown hare (Lepus europaeus)       1.0   1.4
European badger (Meles meles)               0.5   2.0
Domestic cat (Felis catus)                  1.0   2.8
Wild boar (Sus scrofa)                      4.8  19.3
Wild boar (Sus scrofa) juv.                 2.9   5.2    3.1    4.2
Red deer (Cervus elaphus)                   1.4   0.4
Roe deer (Capreolus capreolus)              3.4   1.4
Cervidae, indet.                            1.0   0.8
Small birds (Passeriformes spp.)                         3.1      +
Pheasant (Phasianus colchicus)                           1.5    4.3
Other birds                                 1.4     +    3.1      +
Bird egg                                    0.5   0.1           0.1
Reptiles and amphibians                     2.9   0.2    1.5    0.1
Invertebrates                              14.0   0.2   13.8   11.0
Plum (Prunus domestica)                                  9.2    8.3
Blackthorn (Prunus spinosa)                 1.9   1.4           8.6
Other fruits                                0.5   0.1    4.6    0.4
Maize (Zea mays)                            0.5   0.6    4.6
Other plants                                7.2   2.3   10.8
Number of scats analysed                   75           20
Number of items                           207           65
[B.sub.A]                                   0.19  0.12   0.18   0.07

Food items                                Autumn         Winter
                                          %O      %B     %O      %B

Microtus sp.                               31.0   37.9    40.2   40.4
Bank vole (Myodes glareolus)                7.6    8.1    12.5   12.8
European water vole (Arvicola amphibius)    2.3    4.0     6.0    9.2
Apodemus sp.                               17.6   16.5    15.1   13.1
Other small rodents                         4.2    4.0     3.1    2.5
Shrews (Soricidae)                          0.4    0.2     0.3    0.1
European mole (Talpa europaea)
European brown hare (Lepus europaeus)       0.6    1.1
European badger (Meles meles)                              0.3    0.3
Domestic cat (Felis catus)
Wild boar (Sus scrofa)                      3.0    3.1     2.6   11.0
Wild boar (Sus scrofa) juv.                                0.6    3.3
Red deer (Cervus elaphus)                   1.3    0.1     1.7    1.2
Roe deer (Capreolus capreolus)              0.2      +     2.6    1.8
Cervidae, indet.                            0.4      +     1.1    0.5
Small birds (Passeriformes spp.)            1.3    0.1     0.9      +
Pheasant (Phasianus colchicus)              0.4      +
Other birds                                 0.4      +     0.9      +
Bird egg                                    0.2      +
Reptiles and amphibians                     0.8      +
Invertebrates                               1.9      +     0.6      +
Plum (Prunus domestica)                     1.1   11.2     0.3    0.2
Blackthorn (Prunus spinosa)                 9.3    6.4     0.6    0.1
Other fruits                                4.9    3.1     0.6    0.2
Maize (Zea mays)                            1.3    1.0     1.1    1.3
Other plants                                9.6    3.0     9.1    1.8
Number of scats analysed                  163            115
Number of items                           471            351
[B.sub.A]                                   0.11   0.08    0.07   0.05

Food items                                Annual
                                          %O       %B

Microtus sp.                                32.4   37.2
Bank vole (Myodes glareolus)                 9.0    9.9
European water vole (Arvicola amphibius)     3.8    6.8
Apodemus sp.                                15.4   14.2
Other small rodents                          3.4    2.8
Shrews (Soricidae)                           0.5    0.3
European mole (Talpa europaea)               0.7    0.7
European brown hare (Lepus europaeus)        0.5    0.6
European badger (Meles meles)                0.2    0.5
Domestic cat (Felis catus)                   0.2    0.5
Wild boar (Sus scrofa)                       3.0    8.9
Wild boar (Sus scrofa) juv.                  0.9    2.4
Red deer (Cervus elaphus)                    1.4    0.6
Roe deer (Capreolus capreolus)               1.6    1.0
Cervidae, indet.                             0.7    0.3
Small birds (Passeriformes spp.)             1.0    0.1
Pheasant (Phasianus colchicus)               0.3    0.2
Other birds                                  0.9      +
Bird egg                                     0.2      +
Reptiles and amphibians                      1.0      +
Invertebrates                                4.5      +
Plum (Prunus domestica)                      1.1    1.0
Blackthorn (Prunus spinosa)                  4.6    6.6
Other fruits                                 2.7    1.6
Maize (Zea mays)                             1.3    1.3
Other plants                                 9.0    2.3
Number of scats analysed                   373
Number of items                           1094
[B.sub.A]                                    0.13   0.09

Table 2. Results of log-linear models for the frequencies of occurrence
of food types in the scats of golden jackals (Canis aureus) and red
foxes (Vulpes vulpes) during four seasons and three years (2010-2013)
in Vajszlo, Hungary, for the effect of years, seasons, and their
interaction. P values (with Bonferroni corrections) in boldfaced
type are significant. In case of pheasant (fox) was not enough data to
perform the calculation.

Item           Effect       df  Golden jackal
                                [[chi].sup.2]  P

Small mammals  Year          2           3.04    0.2190
               Season        3           2.67    0.4454
               Interaction   6          29.67  < 0.0001
Brown hare     Year          2           0.24    0.8878
               Season        3           2.32    0.5081
               Interaction   6          29.33  < 0.0001
Carnivores     Year          2           0.01    0.9998
               Season        3           6.10    0.1068
               Interaction   6          29.11  < 0.0001
Wild boar      Year          2           4.09    0.1294
               Season        3          10.68    0.0136
               Interaction   6          30.20  < 0.0001
Cervids        Year          2           0.71    0.7017
               Season        3          12.48    0.0059
               Interaction   6          29.53  < 0.0001
Pheasant       Year          2           0.36    0.8357
               Season        3           4.62    0.2016
               Interaction   6          28.95  < 0.0001
Other birds    Year          2           3.91    0.1412
               Season        3           6.81    0.0782
               Interaction   6          28.48  < 0.0001
Reptiles,      Year          2           1.29    0.5249
amphibians     Season        3          11.77    0.0082
and fish       Interaction   6          29.80  < 0.0001
Invertebrates  Year          2           2.03    0.3622
               Season        3          43.97  < 0.0001
               Interaction   6          29.41  < 0.0001
Plants         Year          2           5.83    0.0541
               Season        3          24.85  < 0.0001
               Interaction   6          24.50    0.0004

Item           Effect       Red fox
                            [[chi].sup.2]  P

Small mammals  Year                 1.77     0.4131
               Season              24.90   < 0.0001
               Interaction         56.53   < 0.0001
Brown hare     Year                 3.92     0.1411
               Season               0.43     0.9334
               Interaction         60.66   < 0.0001
Carnivores     Year                 0.60     0.7414
               Season               0.45     0.9307
               Interaction         61.86   < 0.0001
Wild boar      Year                18.61   < 0.0001
               Season               8.02     0.0456
               Interaction         57.74   < 0.0001
Cervids        Year                 0.85     0.6552
               Season               1.00     0.8021
               Interaction         62.22   < 0.0001
Pheasant       Year
Other birds    Year                 5.80     0.0549
               Season               5.69     0.1278
               Interaction         63.47   < 0.0001
Reptiles,      Year                 0.88     0.6438
amphibians     Season               6.04     0.1098
and fish       Interaction         61.93   < 0.0001
Invertebrates  Year                 1.88     0.3911
               Season              63.42   < 0.0001
               Interaction         58.27   < 0.0001
Plants         Year                 0.74     0.6908
               Season              93.18   < 0.0001
               Interaction         45.96   < 0.0001

Table 3. Seasonal and annual relative frequency of occurrence and
biomass percentage of food items in scats of red foxes (Vulpes vulpes)
in Vajszlo, Hungary. For abbreviations see Table 1.

Food items                                Spring         Summer
                                          %O      %B     %O      %B

Microtus sp.                               26.2   33.6     7.7   15.3
Bank vole (Myodes glareolus)                1.6    2.6     2.9    1.9
European water vole (Arvicola amphibius)   11.9   22.6     1.9    2.1
Apodemus sp.                                5.6    2.5     3.8    1.6
Other small rodents                         1.6    1.1
Shrews (Soricidae sp.)                      0.8    0.1     1.9    1.2
European mole (Talpa europaea)              0.8    0.7     1.9    1.7
European brown hare (Lepus europaeus)       1.6    4.3
Small mustelids (Mustelidae)
Domestic dog and cat                        1.6    7.1
Medium sized mammal, indet.                 2.4    1.3
Wild boar (Sus scrofa)                      2.4    0.5
Wild boar (Sus scrofa) juv.                 1.6    9.7
Red deer (Cervus elaphus)                   0.8      +     1.0    0.8
Roe deer (Capreolus capreolus)              0.8      +
Small birds (Passeriformes sp.)             2.4    0.5     3.8    0.4
Pheasant (Phasianus colchicus)
Anas sp.                                    0.8    0.9     1.0    0.1
Other medium sized birds                    6.3    9.1     1.0    9.1
Bird egg                                    2.4      +
Reptiles                                    3.2    0.1     3.8    0.1
Invertebrates                              15.1    0.2    26.9    0.1
Plum (Prunus domestica)                                   11.5   28.9
Blackthorn (Prunus spinosa)                 2.4    1.2
Other fruits                                1.6    1.5    26.0   35.6
Other seeds and plants                      6.3    0.5     4.8    1.1
Number of scats analysed                   66             41
Number of items                           126            104
[B.sub.A]                                   0.24   0.11    0.23   0.10

Food items                                Autumn         Winter
                                          %O      %B     %O      %B

Microtus sp.                               11.0   16.5    32.6   39.4
Bank vole (Myodes glareolus)                2.2    2.7     2.8    1.2
European water vole (Arvicola amphibius)    1.5    1.2     4.5    5.6
Apodemus sp.                               14.7   10.3     9.0    8.1
Other small rodents                         2.9    2.0     6.2    8.2
Shrews (Soricidae sp.)                                     1.7    2.0
European mole (Talpa europaea)                             0.6    0.3
European brown hare (Lepus europaeus)                      1.1    0.1
Small mustelids (Mustelidae)                               1.1    8.4
Domestic dog and cat
Medium sized mammal, indet.
Wild boar (Sus scrofa)                                     6.2    5.9
Wild boar (Sus scrofa) juv.                                2.2    7.8
Red deer (Cervus elaphus)                                  1.1    0.2
Roe deer (Capreolus capreolus)              2.2      +     3.4    0.4
Small birds (Passeriformes sp.)             1.5      +     5.1    1.0
Pheasant (Phasianus colchicus)                             0.6      +
Anas sp.                                    1.5    0.4     0.6      +
Other medium sized birds                    0.7      +     3.9    2.8
Bird egg                                                   0.6      +
Invertebrates                               4.4      +     0.6      +
Plum (Prunus domestica)                     5.1    6.8
Blackthorn (Prunus spinosa)                23.5   36.5    10.1    7.7
Other fruits                               11.0   17.9     1.1      +
Other seeds and plants                     17.6    5.6     5.1    0.8
Number of scats analysed                   59            102
Number of items                           136            178
[B.sub.A]                                   0.09   0.04    0.20   0.10

Food items                                Annual
                                          %O      %B

Microtus sp.                               21.0   28.8
Bank vole (Myodes glareolus)                2.4    2.0
European water vole (Arvicola amphibius)    5.0    8.2
Apodemus sp.                                8.6    6.1
Other small rodents                         3.1    3.7
Shrews (Soricidae sp.)                      1.1    1.0
European mole (Talpa europaea)              0.7    0.6
European brown hare (Lepus europaeus)       0.7    1.1
Small mustelids (Mustelidae)                0.4    3.0
Domestic dog and cat                        0.4    1.7
Medium sized mammal, indet.                 0.6    0.3
Wild boar (Sus scrofa)                      2.6    2.3
Wild boar (Sus scrofa) juv.                 1.1    5.2
Red deer (Cervus elaphus)                   0.7    0.2
Roe deer (Capreolus capreolus)              1.8    0.2
Small birds (Passeriformes sp.)             3.3    0.5
Pheasant (Phasianus colchicus)              0.2      +
Anas sp.                                    0.9    0.3
Other medium sized birds                    3.1    4.8
Bird egg                                    0.7      +
Reptiles                                    1.5      +
Invertebrates                               9.9    0.1
Plum (Prunus domestica)                     3.5    6.4
Blackthorn (Prunus spinosa)                 9.7   11.2
Other fruits                                8.5   10.3
Other seeds and plants                      8.5    1.8
Number of scats analysed                  268
Number of items                           544
[B.sub.A]                                   0.19   0.09

Table 4. Distribution of animal food types in the diet of golden jackals
(Canis aureus) and red foxes (Vulpes vulpes) on the basis of weight,
zonation, habitat type and environment association of animal food
species in Vajszlo, Hungary. %O--relative frequency of occurrence,
%B--percentage of consumed biomass. Significance was tested by G-test.

Prey characteristic               %O
                                  Jackal  Fox   G      df  P

Weight (g)           < 15           10.8  19.7   2.66   1  NS
                     15-50          71.1  52.1   2.95   1  NS
                     51-100          1.1   1.8   0.18   1  NS
                     101-300         5.5   9.7   1.19   1  NS
                     301-1000        1.1   6.1   3.72   1  NS
                     1000 <         10.3  10.5   0.00   1  NS
Zonation             Terrestrial    92.6  80.5   0.84   1  NS
                     Arboreal        2.6  10.8   5.41   1  < 0.05
                     Aquatic         4.8   8.7   1.11   1  NS
Habitat type         Open           12.8  43.9  18.06   1  < 0.001
                     Mixed          50.1  52.1   0.04   1  NS
                     Forest         37.1   3.9  30.89   1  < 0.001
Environment          Wild           92.2  72.1   2.47   1  NS
association          Mixed           7.3  26.6  11.65   1  < 0.001
                     House           0.4   1.3   0.44   1  NS

Prey characteristic               %B
                                  Jackal  Fox   G      df  P

Weight (g)           < 15            3.3   3.9   0.04   1  NS
                     15-50          70.5  53.4   2.37   1  NS
                     51-100          0.8   0.9   0.01   1  NS
                     101-300         8.2  14.7   1.87   1  NS
                     301-1000        0.2  11.8  14.46   1  < 0.001
                     1000 <         17.0  15.3   0.09   1  NS
Zonation             Terrestrial    92.0  80.2   0.81   1  NS
                     Arboreal        0.1   7.6   9.54   1  < 0.01
                     Aquatic         7.8  12.2   0.94   1  NS
Habitat type         Open           11.4  56.4  32.61   1  < 0.001
                     Mixed          54.1  40.6   1.93   1  NS
                     Forest         34.5   3.0  31.24   1  < 0.001
Environment          Wild           98.1  85.8   0.83   1  NS
association          Mixed           1.5  11.4   8.66   1  < 0.01
                     House           0.4   2.9   2.12   1  NS
COPYRIGHT 2016 Institute of Vertebrate Biology ASCR
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2016 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Author:Lanszki, Jozsef; Kurys, Anita; Szabo, Laszlo; Nagyapati, Nikolett; Porter, Laura B.; Heltai, Miklos
Publication:Folia Zoologica
Article Type:Report
Geographic Code:4EXHU
Date:Dec 1, 2016
Previous Article:Nutlet is a little nut: disclosure of the phylogenetic position of Robbins' house bat Scotophilus nucella (Vespertilionidae).
Next Article:Recovery of brown trout populations in streams exposed to atmospheric acidification in the Bohemian Forest.

Terms of use | Privacy policy | Copyright © 2019 Farlex, Inc. | Feedback | For webmasters