Abstract
A total of 468 adult Dermacentor reticulatus ticks (298 females and 170 males) collected by flagging in the forests of Lubelskie province, eastern Poland, were analyzed by PCR and nested-PCR for the presence of Babesia microti DNA. In all, 21 ticks (4.5%) were found to be infected with B. microti. The infection rate in females (5.0%) was slightly greater than in males (3.5%). Detection of B. microti for the first time in adult D. reticulatus ticks suggests that this species should be considered as a potential vector of B. microti in Europe.
Introduction
Materials and Methods
Collection of ticks
Unfed D. reticulatus ticks (males and females) were collected during the spring and summer of 2008 and 2009 from the forested areas of five districts of the Lublin region. Of these, two districts (Parczew and Włodawa) harbored wet lakeland forests, while the other three districts (Zamość, Puławy, and Lublin) harbored dry upland forests. The ticks were collected by dragging a woolen flag over lower vegetation at the peripheral and inner parts of deciduous and mixed forests, including suburban localities and recreational areas. The ticks were collected alive and stored at −20°C for further investigation.
DNA isolation
A total of 468 D. reticulatus ticks (298 females and 170 males) were examined. Protozoan DNA was isolated from ticks after removal from alcohol by boiling in 100 μL of 0.7 M ammonium hydroxide for 20 min, and evaporating for 15 min, according to the method of Rijpkema and associates (1996), and stored at −20°C for further analysis.
Detection of Babesia microti DNA by PCR and nested-PCR
Tick lysates were examined for the presence of B. microti DNA using amplification by PCR and confirmatory re-amplification by nested-PCR. The following sets of primers were applied: a pair of outer primers: Bab1 (5′-CTT AGT ATA AGC TTT TAT ACA GC-3′) and Bab4 (5′-ATA GGT CAG AAA CTT GAA TGA TAC A-3′); and a pair of inner primers: Bab2 (5′-GTT ATA GTT TAT TTG ATG TTC GTT T-3′) and Bab3 (5′-AAG CCA TGC GAT TCG CTA AT-3′). These primers are specific for a gene encoding the nuclear small subunit ribosomal RNA (SS-rDNA; Stańczak et al. 2004), and were previously described by Persing and colleagues (1992).
Each PCR reaction was done in a 25-μL reaction volume which contained the following mix of reagents: 0.625 U Taq DNA polymerase (QIAGEN, Valencia, CA), 1× PCR buffer containing 15 mM MgCl2, 0.625 μL 2 mM dNTP (final concentration 0.05 mM; Fermentas, Vilnius, Lithuania), 1 μL 10 μM each of primer Bab1 and Bab4 (Eurogentec, Seraing, Belgium), 2.5 μL of DNA, and nuclease-free water (Applied Biosystems, Foster City, CA). DNA of B. microti merozoites (obtained from the Department of Parasitology, University of Warsaw) was used as a positive control and nuclease-free water as a negative control. The size of the amplified DNA fragment was 238 base pairs (bp).
Nested PCR reactions were carried out under the same conditions with 1 μL of the first amplification product, and with 1 μL 10 μM of each inner primer Bab2 and Bab3. The size of the amplified DNA fragment was 154 bp.
The amplification and re-amplification were carried out in a PTC-150 thermal cycler (MJ Research Inc., Waltham, MA) according to the method of Stańczak and associates (2004). Products of amplification and re-amplification were identified in 2% and 2.5% agarose gel, respectively, after electrophoresis in standard conditions and staining with ethidium bromide solution (2 μg/mL). The amplified fragments were visualized in a transilluminator under UV light (UV-953; JW Electronics, Warsaw, Poland).
DNA sequencing was performed with 38% (8 out of 21) of randomly-selected positive samples with an ABI PRISM 310 Genetic Analyzer (Applied Biosystems) using ABI PRISM Big Dye Terminator v. 3.1. Cycle Sequencing Kits, and Big Dye XTerminator Purification Kits (Applied Biosystems). The results were compared with sequences in the GenBank database using the BLAST server at the National Center for Biotechnology Information (Bethesda, MD).
Statistical analysis
The data were analyzed by chi-square testing and Student's t-test with the use of STATISTICA for Windows v. 5.0 (StatSoft Inc., Tulsa, OK).
Results
Out of 468 adult Dermacentor reticulatus ticks, 21 (4.5%) were found to be infected with Babesia microti. The infection was found in 15 females out of 298 (5.0%) and in 6 males out of 170 (3.5%). There was no statistically significant difference between the prevalence of B. microti in females and males of D. reticulatus (p>0.05).
The sequence analysis of positive samples obtained from D. reticulatus confirmed that the amplified products showed 97–99% homology with known B. microti sequences, accession numbers AB366158.1 (99% homology with a B. microti gene for 18S ribosomal RNA, strain: Munich), and EU882727.1 (97–98% homology with a B. microti 18S ribosomal RNA gene isolated from I. ricinus), for 6 and 2 samples, respectively.
Discussion
Dermacentor reticulatus (syn. Dermacentor pictus) occurs in Eurasia in two areas. Its eastern, main area covers northern Asia and northeastern Europe, from the Yenisei River in Siberia to the Vistula River in Poland, while its western, more isolated area covers England, France, the Netherlands, Belgium, Switzerland, and southwestern Germany (Siuda 1993; Nijhof et al. 2007; Cochez et al. 2011). Most likely, the species is migrating from its main area westward, as it was recently detected in western Poland (Nowak 2011), and Austria (Sixl et al. 2003; Dobler et al. 2008). D. reticulatus is a known vector of Babesia species, causing babesiosis (piroplasmosis) in cattle, horses, and dogs (B. bovis, B. bigemina, B. caballi, B. canis, and Theileria [Babesia] equi; Arthur 1963; Wall and Shearer 2001; Sawczuk 2006; Silva et al. 2010), but so far it has not been associated with human babesiosis caused by B. microti or B. divergens. Welc-Falęciak and associates (2008) detected the presence of B. microti in 11.8% of partly-engorged larvae, and 4.0% of partly-engorged nymphs of D. reticulatus feeding on rodents in the Mazury Lakes District of northern Poland. Walter (1982) was not successful in the experimental transmission of B. microti into golden hamsters by infected nymphs of D. reticulatus.
So far, B. microti has not been reported in the adult D. reticulatus ticks that feed on large animals and less commonly on humans. Nijhof and colleagues (2007) did not find B. microti in 72 D. reticulatus ticks in the Netherlands, and Zygner and co-workers (2010) did not detect B. microti in 381 adult D. reticulatus ticks collected from dogs in Warsaw. Recently, Cochez and associates (2011) did not detect Babesia spp. in 282 D. reticulatus ticks collected in Belgium. Thus, Ixodes ricinus is regarded as the most important vector of B. microti and B. divergens in Europe. It has been shown that in Poland 3–15.3% of adult I. ricinus ticks are infected with B. microti (Skotarczak and Cichocka 2001; Skotarczak et al. 2002; Stańczak et al. 2004; Siński et al. 2006; Wójcik-Fatla et al. 2006; Zygner et al. 2010), while in other central and western European countries the incidence is slightly lower, in the range of 0.1–11.0% (Duh et al. 2001; Foppa et al. 2002; Kalman et al. 2003; Hartelt et al. 2004; Nijhof et al. 2007). Among other ticks, Ixodes trianguliceps was suspected as a possible vector of B. microti, but its role seems to be marginal because of the rare occurrence of this species (Karbowiak 2004; Siński et al. 2006).
In the present study, Babesia microti was detected in adult D. reticulatus ticks that feed on humans and large domestic and wild animals (e.g., cattle, deer, and elk). Thus our findings suggest that this tick species should be considered as a potential vector of B. microti that may cause human babesiosis. The research by Plesman and colleagues (1979) indicates that deer are not a reservoir of B. microti, but the role of cattle in this regard is unknown and requires further study.
Footnotes
Author Disclosure Statement
No competing financial interests exist.
