Natural alveolar echinococcosis with Echinococcus multilocularis in ...

Sci Parasitol 12(1):11-21, March 2011

ORIGINAL RESEARCH ARTICLE

ISSN 1582-1366

Natural alveolar echinococcosis with Echinococcus multilocularis in wild rodents

Sándor Sikó Barabási1, Levente Marosfői2, Zsombor Sikó Barabási3, Vasile Cozma4

1 – Veterinary and Food Safety Authority Covasna, Ciucului Street 149, Sfântu Gheorghe 520036, Romania. 2 – Veterinary and Food Safety Laboratory Harghita, Progresului Street 14, Miercurea Ciuc 530240, Romania. 3 – Echino-News Association, Ciucului Street 149, Sfântu Gheorghe 520036, Romania. Correspondence: Tel. +40722-700699, Fax +40267-312315, E-mail [email protected] 4 – University of Agricultural Sciences and Veterinary Medicine, Faculty of Veterinary Medicine, Department of Parasitology and Parasitic Diseases, Calea Mănăştur 3-5, Cluj-Napoca 400372, Romania

Abstract. Echinococcus multilocularis is the most pathogenic species of Echinococcus with a zoonotic potential in Europe. The adult stage infects the intestine of the natural definitive host (red foxes, Vulpes vulpes). The larval cestode inhabits mainly the liver of natural intermediate hosts, especially wild rodents (Cricetidae, Muridae). The intermediate hosts are infected by ingesting eggs shed with feces of the definitive host. This study shows the presence of the E. multilocularis larval form in the wild rodents from Romania. From the 552 examined wild rodents we found 3.1% (n=17) with cystic liver lesions. A percent of 76.5 (n=13) of them were confirmed to be E. multilocularis cysts.

Keywords: rodents; Arvicolidae, Muridae; Alveolar echinococcosis; larval cestode; Echinococcus multilocularis. Received 04/12/2010. Accepted 04/03/2011.

pedoclimatic conditions to those in Western Europe.

Introduction Alveolar hydatidosis produced by the larval form of Echinococcus multilocularis in wild rodents (mainly Arvicolidae and Muridae families) as main intermediate hosts, was described in France, Switzerland and Austria with a high incidence (9-39% in Arvicola terrestris, respectively 10-21% in Microtus arvalis) (Pétavy and Deblock, 1983; Bonnin et al., 1986; Hofer et al., 2000; Gottstein et al., 2001; Pétavy et al., 2003).

During studies performed between 1991-1995 in the subalpine region of the East Carpathian Mountains, E. multilocularis was for the first time described in wild rodents in Romania by morphological identification of larval stages containing protoscoleces (2 of 422 Microtus nivalis and in 6 Arvicola terrestris, 3 Chionomys arvalis and 2 Clethrionomys glareolus from 2,416 examined wild rodents) (Sikó Barabási, 1992; 1993; Sikó Barabási et al., 1995). Furthermore, larval cestodes with alveolar structures were described in sheep and horses;

Ecoregions of Transylvania inhabited by these rodents are identical in terms of weather and 11



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however, the species diagnosis of these findings was not confirmed to specific level (Sikó Barabási and Cozma, 2008). The presence of E. multilocularis was confirmed also in red foxes from Romania (Sikó Barabási et al., 2010a; 2010b).

Captured individuals identified to species level and euthanized with intraperitoneal T61. The liver of all rodents was examined with a frontal magnifier for the detection of larval E. multilocularis or other larval forms of cestodes. Those with macroscopic changes were fixed in 10% neutral formalin. For the histopathological examination all samples were included in paraffin. Embedded tissue fragments were sectioned using a microtome at 4-5 μm, making serial sections of all anatomical structures of the liver to reflect the existing alveolar cysts and other associated histological lesions. A total of 268 slides were made for histopathological examination. De-waxing, clarifying, hydrating and staining of sections were carried out by regular techniques. Histological and histochemical stains applied were: hematoxylin-eosin (HE), Masson Trichromic (MT), Alcian-blue PAS, Van Gieson Stain (VG), Pappenheim, Koss, Lillie-Pasternack and Toluidine blue (TB) (Satoh, 2005; Marosfői, 2007, Yamasaki, 2008). Histological examinations focused on the differentiation from other cystic structures in the liver (i.e. presence of hooks) (Pétavy et al., 2003; Ito et al., 2010).

In this paper, we systematically investigated wild rodent populations from different ecoregions of 15 Transylvanian counties for cystic parasitic lesions in the liver with emphasis on alveolar echinococcosis. Materials and methods Between August 2007 and July 2010 we followed the spatial (geographical and territorial features) and temporal dynamics (in different months and seasons) of rodent populations from Arvicolidae and Muridae families as the main potential intermediate hosts in the infestations with E. multilocularis. The study was conducted in 15 counties from Transylvania. To follow the parasites spatial and ecological dynamics, the 15 counties were divided into ecoregions. To ensure the conditions for catching, pathological examination, identification and preservation of samples were performed in the field. A total number of 120 traps of two types (wooden box and wire) were used.

Results and discussion Spatial and ecological dynamics of catches Of the total of 3600 traps, 16.3% had made catches. The largest average catch (25%) was during autumn (August-October), followed by summer (May-July) (20%). The minimum catches (10%) were made during the winter (November-January) and spring (FebruaryApril) (table 1).

We used traps in each of the four seasons (spring, summer, autumn and winter) in each of the 15 counties (every month, 20 traps in each five counties). They were either in line or randomly placed, with a distance between them averaging 10 m; traps were left at their locations for 36-48 hours. Thus, during the investigation period a total number of 3600 traps were placed. The traps were set with different baits: smoked bacon, cheese, pieces of cake with walnuts, various seeds, nutmeg, parsley (preferred bait of Arvicola terrestris) pieces of fish or even dog food chips with different flavors. Preferred biotopes of wild rodents such as wooded areas of plateaus and hills, plain bushes, along the rivers or lakes, farmlands etc. were chosen as locations for placing the traps. Traps were placed in areas known with fox dens (Hansson, 1977; Telleira et al., 1991; Benedek, 2007; Murariu, 1987).

Table 1. The number of placed traps/catches Year

Season

Traps

2007

Autumn Winter Spring Summer Autumn Winter Spring Summer Autumn Winter Spring Summer

300 300 300 300 300 300 300 300 300 300 300 300 3,600

2008

2009

2010 Total

12

Total 600

1200

1200

600 3,600

Captured rodents 22 51 28 58 73 29 33 68 78 35 35 77 587

Total 73

188

214

112 587



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In the ecoregion of Someșului and Crișurilor plains (partially Bihor, Satu Mare and Maramureș counties) the majority of caught rodents (62.6%) were from Cricetidae family with the dominating species M. arvalis (74.6%), followed by A. terrestris (20.7%), Microtus agrestis (3%) and Pitymys subterraneus (1.7%). The second rodent family was represented by Muridae (26.8%): Apodemus spp. (48.8%), Micromys minutus (30.8%), Mus musculus (14.4%), Rattus norvegicus (4%) and R. rattus (2%). Family Gliridae corresponded to 2.0% of the total catch. The rest of the catch belonged to the non-rodent family Soricidae (8.6%). The richest catches were recorded in arable land regions segmented with forests and orchards. There was also an annual fluctuation of species in the detriment of others, reported also by Benedek (2007; 2008b). Similar results were described by Murariu (1987) and Sike et al. (2001) in Satu Mare County on micromammal community research from the ingluvial contents of the barn owl (Tyto alba).

In the ecoregion of Eastern Carpathian Mountains (partially Bistrița-Năsăud, Harghita, Covasna and Brașov counties), as a result of relatively high annual humidity the most abundant species was A. agrarius (74.5%), followed by A. flavicollis (18.2%) and A. sylvaticus (3.2%). The frequency of M. arvalis was 4.1%. High abundance of the genus Apodemus in this ecoregion has been reported also by Gurzău and Benedek (2005). In the ecoregion area of Banatului Hills (partially Timiș and Hunedoara counties) most species have been found at low altitudes, in forested areas: C. glareolus (45%), A. flavicollis (34%), A. terrestris (Linnaeus, 1758) – 8.6%, Microtus agrestis (Linnaeus, 1761) – 6.8% and C. nivalis (5.6%). Similar studies in the area were performed by Benedek and Drugă (2005). Ecoregion of Southern Carpathians (partially Hunedoara, Sibiu and Brașov counties) is characterized by a high proportion of forest habitat. The dominating species was A. flavicollis (44.2%), followed by A. agrarius (18.7%), M. arvalis (28.6%) and A. terrestris (7.5%). The rest of the species from the Cricetidae and Muridae families were under 1%. After Benedek et al. (2002) and Antonie et al. (2010), in the Sibiu area, the predominant micromammal from forest habitats is A. flavicollis, followed by A. agrarius.

In the ecoregion of Apuseni Mountains and Crișana Hills (partially Sălaj, Cluj, Alba, Arad and Bihor counties) the main catch was Apodemus flavicollis (58.6%) followed by A. terrestris (21.2%), M. arvalis (18.3%) and C. glareolus (1.9%). The relative abundance of A. flavicollis is due to relatively low altitudes and proper environment (Benedek et al., 2005; Benedek, 2007; 2008b).

The dynamics of spatial distribution of rodents as regards diversity of species and abundance of catch was higher on lower altitudes, agricultural lands and along rivers compared to mountainous and hilly areas. The same situation was recorded by Benedek (2007; 2008b) who showed that there are significant fluctuations in population densities of rodents from year to year. Similar records were published by Telleira et al. (1991), Todd et al. (2000), Sevianu and Coroiu (2004), Kecskés (2004).

In the ecoregion of the Transylvanian Plateau (partially Cluj, Mureș, Harghita, Alba, Hunedoara, Bistrița-Năsăud counties) the variety of habitats (both natural and anthropogenic) was reflected in the diversity of the catch, reported also by Benedek (2007; 2008b): A. terrestris (35.8%), A. flavicollis (29.6%), A. agrarius (14.3%), A. sylvaticus (16.5%) and C. glareolus (3.8%). In intensively cultivated agricultural areas the catch was represented by M. arvalis (72.4%), A. sylvaticus (12.2%), A. agrarius (5.6%) and A. terrestris (9.8%). The variety of habitats (both natural and anthropogenic) of this ecoregion is also reflected in the structure of small rodent communities. Specific diversity is high and the share of the species is relatively balanced. (Benedek, 2008a).

In woodland habitats the rodents identified with high frequency was A. flavicollis. This species shows a preference for habitats with woody vegetation: forest, scrub, selvedges. Conversely, A. sylvaticus mainly occupies the wooded habitat in which they can reach high densities during winter (Todd et al., 2000). 13



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On open lands the most abundant species was M. arvalis (32.4). Although the number of traps placed in different ecoregions was equal, the difference of over 10% of the share of the majority of species might be explained by Benedek (2008a; 2008b) by different behavioral patterns. Forest species, which are used to fast changes occurring in their environment, fall into traps almost immediately after installation. Species in open areas are more suspicious, more reluctant to new objects in their habitat, avoiding them. In order to be caught the traps should be left for longer time in the same place.

Finally the fourth category of habitat is the low altitude and high humidity during the whole year. The most representative species of this habitat was A. agrarius which in these areas reached 74.5% of the total catch. They climb the mountains along the river but just on the lower part. Table 2 shows the overall data on the captured potential intermediate host species by county. Prevalence of alveolar echinococcosis Following morphological examinations performed immediately after the capture of a total number of 552 rodents (potential intermediate hosts) macroscopic changes were detected in the liver of 17 (3.1%) animals. Greater prevalence of cystic changes in the liver was found in catches from Satu Mare (10.5%) and Timiș counties (8.0%) (table 3). In the infected rodent species dominance of four species was found with a prevalence between 1.1% and 8.7% (table 4). In two A. terrestris samples and one M. arvalis sample macroscopically glomerular formations were found just below the liver surface under the Glisson’s capsule, like a conglomerate of cysts (figure 1), similar to a cauliflower (figure 2), with well highlighted area, dirty yellowishwhite color, with vesicle diameter ranging from 1-6 mm.

Particular interest is raised by the influence of the intensive and traditional farming practices on the ecology of M. agrestis. The few number of captured field vole could be explained by their life as an unspecialized opportunist in a variety of habitat types (Hansson, 1977; Erlinge et al., 1990). Between the two categories lies the bank vole C. glareolus which is widespread in forested areas and areas at high altitudes (19.86%), but they do not develop high density populations. The forest destruction generated the local extinction of the bank vole.

Table 2. Rodents captured for this study (n) County

Species

Total

AB

AR

BH

BN

BV

CJ

CV

HR

HD

MM

MS

SM

SJ

SB

TM

-

-

5

-

-

-

-

-

-

-

-

-

-

-

-

5

Cricetidae

27

16

44

4

5

27

4

19

43

7

19

34

8

6

17

280

C. glareolus

3

-

-

-

-

-

-

-

26

-

-

-

-

-

5

34

A. terrestris

3

8

14

4

2

14

9

8

3

5

15

8

3

7

103

M. arvalis

21

8

30

-

3

13

4

10

5

4

14

17

-

3

-

132

M. agrestis

-

-

-

-

-

-

-

-

-

-

-

2

-

-

5

7

C. nivalis

-

-

-

-

-

-

-

-

4

-

-

-

-

-

-

4

Muridae

37

6

17

19

19

21

33

31

26

5

9

4

23

9

8

267

M. minutus

-

-

4

-

-

-

-

-

-

-

-

2

-

-

-

6

A. sylvaticus

10

-

-

5

1

-

-

10

2

2

-

-

-

-

-

30

A. flavicollis

15

6

13

6

11

13

5

7

19

3

-

2

23

5

8

136

A. agrarius

12

-

-

8

7

8

28

14

5

-

9

-

-

4

-

95

TOTAL

64

22

66

23

24

48

37

50

69

12

28

38

31

15

25

552

Other families

14



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Table 3. The prevalence of gross cystic lesions in the liver of rodents by county County Arad Bihor

Total capture (n) 22 66

1 4

Prevalence (%) 4.5 6.1

Positive (n)

Covasna

37

2

5.4

Harghita

50

2

4.0

69 38 25 307

2 4 2 17

2.8 10.5 8.0 5.5

Hunedoara Satu Mare Timiș Total

Table 4. The prevalence of hepatic lesions by species Species of rodent A. terrestris C. glareolus M. arvalis A. agrarius Total

Captured (n) 103 34 132 95 364

Positive (n) 9 2 5 1 17

Species of rodent (n) A. terrestris (1) A. terrestris (1) M. arvalis (3) M. arvalis (1) A. agrarius (1) A. terrestris (1) M. arvalis (1) C. glareolus (2) A. terrestris (4) A. terrestris (2)

Ci-Peng et al. (2005) made a classification of these cysts into three types; large circumscribed mass types were more common (67.8%) and the other two more rare: nodular types (16.7%) and mixed types (15.5%).

Prevalence (%) 8.7 5.9 3.8 1.1 4.7

Histological description of lesions The larval cestodes of E. multilocularis from the liver of voles produce a typical infiltration and induce destruction of the organ. The intermediate hosts respond with a granulomatous inflammatory reaction and peripheral formation of granulation tissue. In centripetal direction, the adventitial layer’s components were formed by the fibroconjunctive reaction; the inflammatory cells were present. In the peripheral areas the lymphocytes and monocytes were dominating. They were followed by a rich infiltration of the giant cells and a decrease of the inflammatory local reaction (figures 9, 10). These structures were gradually changed by the fibroconjunctive reaction.

The number of cystic formations found in the livers of rodents, their size and form as well as their structure are shown in table 5. Extrahepatic disease was very rare (1%). The most frequent morphological profile of alveolar echinococcosis was represented by an intrahepatic heterogeneous, infiltrative and destructive mass, with irregular outlines and a non-vascular and necrotic center. The cyst appears as a spongy structure, resembling a crumb or cheese (figures 3, 4), with empty cavities or with a grey and jelly content. Most of the cavities do not have a well-defined content. In other samples, the formation had mainly a cystic structure, without a divided multivesicular character (figure 5).

The cuticular layer was mono- or multistratified, formed by concentric conjunctival tissue layers, which penetrated in the cystic cavity and developed many anastomoses conferring it a multi-vesicular aspect. (figures 11, 12). In the spaces between these blade cell similar to giant cells we could also notice rare histiocytes and eosinophils. (figure 13). Due to the multitude of anastomoses, the cyst is a structure with an invasive character (figure 14). In most cases there were collapsed cysts characterized by a fragmented or folded laminar layer and massive necrosis.

The gross lesions consisted of unilocular cysts (in the case of young cysts), circular or irregular oval forms. The small cysts had dimensions between 100-200 x 250-350 μm. The biggest cysts (1200-1500 μm) usually contained a calcareous deposit, or a jelly substance, moreover an unidentifiable content (figures 6, 7, 8). The monovesicular cysts were rare. The greatest number of them had a complex structure divided by the cuticula in a multivesicular, cavernous or spongy formation.

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Figure 1. Liver of Arvicola terrestris with mildly hypertrophic aspect (“cauliflower-like”). Figure 2. Liver of A. terrestris with a detail of the “cauliflower-like” aspect. Figure 3. Liver of Microtus arvalis - aspect of the cyst after incision. Figure 4. Liver of M. arvalis - detailed aspect of the internal structure of the cyst. Figure 5. Liver of M. arvalis - cyst under the Glisson’s capsule. Figure 6. Liver of M. arvalis - monovesicular cyst (HE, 40x). Figure 7. Liver of C. glareolus - inflammatory pericystic infiltrations and mineralization process inside the cyst (TB, 200x). Figure 8. Liver of A. agrarius - partial calcifications of the alveolar cyst (Koss, 200x).

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Figure 9. Liver of A. terrestris - incision across the alveolar cyst wall; the proligerous membrane has an irregular multi-cellular aspect (VG, 400x). Figure 10. Liver of A. terrestris - inflammatory infiltration with lymphocytes, lymphoblasts, eosinophils, plasmocytes and macrophages. (Pappenheim, 650x). Figure 11. Liver of A. agrarius - the cuticula layer (Pappenheim, 400x). Figure 12. Liver of A. terrestris - pericystic reaction and the cuticula layer (HE, 100x). Figure 13. Liver of A. terrestris - a multinucleated giant cell and granular-vacuolar degeneration of the hepatocytes with anisokaryosis (HE, 650x). Figure 14. Liver of A. terrestris - partially mineralized cyst with another alveolar cyst with an irregular wall (MT, 400x). Figure 15. Liver of A. terrestris - subcapsular alveococcus cyst; notice the proligerous capsule; the proligerous membrane is irregular as a consequence of more intense multiplication of the cells which form budded points (HE, 200x). Figure 16. Liver of A. terrestris - Invading anastomoses (HE, 40x).

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Table 5. The number, size and structure of hepatic cysts

A. terrestris

Number of cysts 3

Size of cysts (mm) 1.0-6.0

C. glareolus

1-5

0.4-1.4

M. arvalis

1-26

0.8-1.6

A. agrarius

1-3

0.3-1.1

Species

The position of cysts Clustered or conglomerate forms subcapsular around the liver mass Isolated under the hepatic capsule Below the capsule of liver or conglomerated inside the liver mass Isolated under the hepatic capsule

The germinative layer which lines the new formed cavities has a plasmatic structure with rarely multinucleate cells (figure 15). This layer had many young cells and gave a rhizoid aspect characteristic for the malignant tissues (figure 16). Some cysts contained remnants of a single germinative layer. The morphological findings described here are consistent with published cases of alveolar echinococcosis in wild rodents (Ohbayashi, 1960; Mehlhorn et al., 1983; Pétavy and Deblock, 1983; Bonnin et al., 1986; Pétavy et al., 2003).

Thickness and structure Adventitia Membrane 15-30 μm 80-100 μm, rich in inflammatory cells Rich in fiber cells, 2-10 μm 20-100 μm 5-15 μm Predominance of fibrous cells, 5-20 μm Poor in cells 1-4 μm

lymphocytes, plasma cells and giant cells, forming a typical alveococcus nodule. The alveolar echinococcosis lesions in the liver behave like a slow growing liver cancer. Although the liver is the most frequently involved organ, blood dissemination to other organs can also occur (Mehlhorn et al., 1983). The right lobe is involved most frequently, with involvement of the porta hepatis. Parasitic lesions in the liver can vary from small foci (few mm) to large (15–20 cm) areas of infiltration (Pétavy and Deblock, 1983; Bonnin et al., 1986; Reuter et al., 2001).

Studies aiming the histological aspects have suggested that E. multilocularis produces multilocular alveolar cysts (1–10 mm in diameter) that resemble alveoli. They grow by means of exogenous proliferation with cysts that progressively invade the host tissue by means of peripheral extension of the processes originating in the germinal layer. The larvae cause invasive and destructive changes in the tissue. This area is separated from the hepatic parenchyma by inflammatory cells (Kodama, 2003). The lesions are characterized by many alveoli with different sizes and shapes (Ci-Peng et al., 2005). Observation of alveolus wall showed that the thick, non-cellular laminated outer layer looked bank-like, sometimes folding within the alveolar cavity. The thin, germinal inner membrane lined by a single layer cell was usually deficient due to detachment. Brood capsule or protoscolices were occasionally seen. The lesion may be complicated by central necrosis, producing a cavity or pseudocyst after liquefaction. In the periphery of alveoli group there was hyperplasia of fibro-connective tissue and cellular infiltration of eosinocytes,

The cystic structure, their size and location look alike the wild rodents cysticercosis produced by Taenia taeniaeformis. Many studies have reported the presence of T. taeniaeformis cysts in wild rodents. Moreover, E. multilocularis and T. taeniaeformis were simultaneously found in the liver of A. terrestris (Deblock and Pétavy, 1983; Hofer et al., 2000). The differential diagnosis is based on the gross and histological characteristics. In contrast to the alveolar echinococcosis morphology, the T. taeniaeformis cysts (strobilocercus) usually develop in hepatobiliary system of a rodent intermediate host. The cyst contained approximately 4.5 x 0.5 cm long larvae without any fluid. The wall was thin but fibrotic. Individual larvae were opaque white and lodged in close curvilinear arrangements. Their identity is revealed upon opening the cysts, when they burst out. Two crowns of hooks were observed on the scolex. The total number of hooks was 36 and their size was 0.36-0.44 mm on the anterior crown and 0.25-0.27 mm on the posterior one. The repartition of the liver cysts is shown in table 6. 18



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Table 6. Etiology of liver cysts in the examined rodents E. multilocularis Species Liver cysts (n) T. taeniaeformis Glomerular Cystic A. terrestris 9 2 7 C. glareolus 2 1 1 M. arvalis 5 1 1 3 A. agrarius 1 1 Total 17 3 10 4

Pétavy et al. (2003) have reported similar results (table 7).

intermediate hosts of primary importance for the transmission of E. multilocularis in Romania.

Table 7. Etiology of liver cysts in the examined rodents after Pétavy et al. (2003): E. multilocularis (EML); T. taeniaeformis (EMTTL) Rodent species A. terrestris C. glareolus M. arvalis A. sylvaticus

Examined rodents (n) 1730 11 66 22

EML

EMTTL

60 2 2 0

3 0 0 0

References Antonie I., Spânu S., Iliu A., Timar A. 2010. Researches regarding the biologic reserve of the rodent Microtus arvalis Pall (Rodentia: Microtidae) during the autumn of 2009 in the Orchards in Sibiu county. The 39th International Session of Scientific Communications of the Faculty of Animal Science, Bucharest, Romania Scientific papers (series D; vol. LIII). Animal Science, pp. 86-91. Benedek A.M. 2007. Ecological niches habitat dimension of terrestrial small mammals in Transylvania (Romania). Hystrix It. J. Mamm. Suppl. 5th European Congress of Mammology: p. 533. Benedek A.M. 2008a. Small mammals (Ordo Insectivora and Ordo Rodentia) from AgnitaSighişoara area (Romania). Transylv. Rev. Syst. Ecol. Res. 3. Benedek A.M. 2008b. Small mammals (Ordo Insectivora and Ordo Rodentia) from Transylvania (Romania) [Studii asupra mamiferelor mici (Ordinele Insectivora și Rodentia) în Transilvania-România] [in Romanian]. PhD thesis. Universitatea din București, Romania. Benedek A.M., Drugă M. 2005. Data regarding the small mammal communities (Mammalia: Insectivora et Rodentia) from Râu Şes River Basin (Ţarcu and Godeanu Mountains, Romania). Trav. Mus. Nat. His. Nat. Gr. Antipa 48:321-329. Benedek A.M., Sârbu I., Vasile M., 2005. Small mammals (Ordo Insectivora and Ordo Rodentia) from the Apuseni Mountains Natural Park area (Western Carpathians, Romania). Stud. Com. Biol. 6:116-121. Benedek A.M., Soricu M., Drugă M. 2002. Preliminary data regarding the small mammal populations (Ord. Insectivora and Ord. Rodentia) in Sibiu Depression. Acta Oecol. Sibiu 9:11-24.

In seven cases (53.8%) a few invaginated protoscolices (60-100 μm diameter) were present. The samples confirmed to be infected with E. multilocularis originated from the same geographic area where the adult stage of the parasite was found in foxes (Sikó Barabási et al., 2010a; 2010b). The origin of positive samples is as following (in parentheses the county): A. terrestris Fântânele (AR) 46°07’48.64”N 21°23’10.40”E; Râpa (BH) 46°46’33.08”N 22°00’51.93”E; Belfir (BH) 46°43’56.28”N 21°57’13.54”E; Sânmărghita (CJ) 47°09’54.13”N 23°59’58.80”E; Sanislău (SM) 47°36’50.25”N 22°19’46.66”E; Petea (SM) 47°53’21.07”N 22°50’18.68”E; Pelișor (SM) 47°54’30.63”N 22°51’55.15”E; Ţicău (SJ) 47°26’52.23”N 23°18’18.80”E; Seceani (TM) 45°59’08.77”N 21°17’58.54”E; C. glareolus - Ilteu (HD) 46°00’42.19”N 22°22’00.76”E; M. arvalis - Homorog (BH) 46°50’21.95”N 22°43’24.41”E; Chiștag (BH) 47°02’17.85”N 22°21’10.49”E; A. agrarius Dobolii de Jos (CV) 45°46’17.39”N 25°46’15.28”E. We conclude that A. terrestris, C. glareolus, M. arvalis and A. agrarius are suitable 19



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