International Journal of Medical Microbiology
The role of the sand lizard (Lacerta agilis) in the transmission cycle of Borrelia burgdorferi sensu lato
Introduction
Lyme borreliosis (LB) is the most widespread vector-borne disease in the northern hemisphere. The causative agents of LB are spirochetes from the Borrelia burgdorferi sensu lato (s.l.) complex which currently comprises at least 12 genospecies. The main European vector of LB is Ixodes ricinus, the most common tick in Europe. Currently, B. burgdorferi s.s., B. garinii, B. afzelii, and B. spielmanii are clearly established as pathogenic to humans (van Dam et al., 1993; Wang et al., 1999; Földvári et al., 2005). B. valaisiana and B. lusitaniae previously considered as non-pathogenic might cause disease as well (Collares-Pereira et al., 2004; Diza et al., 2004). The geographic distribution of B. burgdorferi s.l. genospecies in Europe is very variable and can vary even in relatively small areas as well as over time in a given area (Derdáková and Lenčáková, 2005). In endemic areas of Europe, at least 6 Borrelia genospecies may circulate between vertebrate hosts and ticks. B. afzelii and B. garinii are the most frequent and the most widely distributed genospecies and occur over the whole of Europe (Hubálek and Halouzka, 1997) followed by B. valaisiana and B. burgdorferi s.s. (Derdáková et al., 2003). B. spielmanii and B. lusitaniae belong to the less abundant genospecies in Europe. Records of B. spielmanii in I. ricinus, in reservoir hosts, and in human patients come from the Netherlands (Wang et al., 1999), the Czech Republic (Derdáková et al., 2003), Germany (Richter et al., 2004), and Hungary (Földvári et al., 2005). The prevalence of B. lusitaniae varies in different parts of Europe. While in the Mediterranean basin it represents the dominant or the only genospecies present in I. ricinus ticks, reports from other parts of Europe are rather rare (Postic et al., 1997; Gern et al., 1999; De Michelis et al., 2000; Younsi et al., 2001; Sarih et al., 2003; Wodecka and Skotarczak, 2005; Poupon et al., 2006; Amore et al., 2007). Particular Borrelia genospecies differ in their transmission cycles with different vertebrate taxons as reservoir hosts. Birds are competent reservoir hosts of B. garinii and B. valaisiana (Humair et al., 1998; Hanincová et al., 2003b). Rodents serve as reservoir hosts for B. afzelii (Humair et al., 1999; Hanincová et al., 2003a) and B. garinii belonging to the OspA type 4 (Postic et al., 1997). The newly described genospecies B. spielmanii is maintained in natural foci by the edible dormouse (Eliomys quercinus) and the fat dormouse (Glis glis) (Matuschka et al., 1994; Richter et al., 2004). Several lizard species were proved to possess a complement with borreliacidal activity (Lane and Loye, 1989; Wright et al., 1998), and therefore the role of lizards in the circulation of B. burgdorferi s.l. has been underestimated. Recent studies suggest associations of lizards with B. lusitaniae circulation. The reservoir competence of Psammodromus algirus was proven recently (Dsouli et al., 2006). B. lusitaniae was detected in skin biopsy specimens and blood samples and in larvae and nymphs of I. ricinus removed from green lizards (Lacerta viridis) (Majláthová et al., 2006) and wall lizards (Podarcis muralis) (Amore et al., 2007). Richter and Matuschka (2006) detected a high prevalence of B. lusitaniae in ticks feeding on L. agilis and Podarcis muralis.
The aim of this study was to demonstrate that the sand lizard (L. agilis) contributes to the maintenance cycle of B. burgdorferi s.l. and to compare 3 distinct populations of L. agilis in Europe.
Section snippets
Study area
The study was carried out during summer of 2006 in 3 distinct localities. The first locality was chosen in Martinské Hole Mountains, Slovakia (49°05′N, 18°49′E). The dominant vegetation consisted of European beech (Fagus sylvatica) and silver fir (Abies alba). Beech is mostly mixed with silver fir, Norway spruce (Picea abies), and sycamore (Acer pseudoplatanus). The climate is cold with high humidity. Lizards were sampled on the forest edges and clearings. The second sampling area was located
Captured lizards and infestation with Ixodes ricinus ticks
During the study, 87 sand lizards were captured at 3 localities in Europe and examined for the presence of I. ricinus ticks.
In Slovakia, 11 (6 females, 2 males, and 3 juveniles) sand lizards were captured. Each lizard was infested by ticks. Altogether, 152 I. ricinus (74 larvae, 78 nymphs) were removed (Table 1). The mean infestation was 13.8 ticks per lizard. The highest number of ticks collected from a single lizard, an adult female, was 29.
Totally, 48 sand lizards (16 females, 16 males, 16
Discussion
The implication and the role of lizards in the maintenance cycle of B. burgdorferi s.l. in the field are currently studied intensively. Specific bonds between B. valaisiana as well as B. garinii and birds, and B. afzelii and rodents were described; however, the specific reservoir host for B. lusitaniae was unknown. Recently, Psammodromus algirus, a small lacertid lizard and the dominant host for immature I. ricinus ticks in Tunisia, was proved to be a reservoir host for B. lusitaniae (Dsouli et
Acknowledgments
Capturing lizards and sample collection were conducted under the permission 12/31.03.2006 issued by Danube Delta Biosphere Reserve Authority (Romania), 6103/2007-2.1/jam issued by the Ministry of Environment of the Slovak Republic, and 12/2007 issued by local ethics committee for animal studies in Poznaň (Poland). This work was financially supported by the Scientific Grant Agency of the Ministry of Education of Slovak Republic and the Slovak Academy of Sciences No. 1/0139/08, by the Slovak
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