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Applied and Environmental Microbiology, October 2007, p. 6166-6171, Vol. 73, No. 19
0099-2240/07/$08.00+0 doi:10.1128/AEM.00590-07
Copyright © 2007, American Society for Microbiology. All Rights Reserved.

H. Gil,2
R. Escudero,2
M. Barral,1
I. Jado,2
R. A. Juste,1
P. Anda,2 and
A. L. García-Pérez1*
NEIKER, Instituto Vasco de Investigación y Desarrollo Agrario, Department of Animal Health and Production, 48160 Derio, Bizkaia, Spain,1 Centro Nacional de Microbiología, Instituto de Salud Carlos III, 28220 Majadahonda, Madrid, Spain2
Received 14 March 2007/ Accepted 26 July 2007
| ABSTRACT |
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| INTRODUCTION |
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A wide range of mammalian reservoir hosts, including rodents, are involved in the natural cycle of various bacterial diseases. Different species of small mammals, mainly mice (Apodemus spp.) and voles (Microtus spp. and Clethrionomys glareolus), are recognized vertebrate reservoirs of tick-borne bacterial zoonoses such as Lyme disease (borreliosis) and human granulocytic ehrlichiosis, among others. In Europe, several rodent species seem to be the natural reservoirs of Borrelia burgdorferi sensu lato (35), Anaplasma phagocytophilum (7, 25), and C. burnetii (44), but there are few reports on the role of such species as possible reservoirs of tick-borne zoonotic bacteria in Spain. The role of small mammals in the biological cycle of B. burgdorferi sensu lato was recently investigated in areas of northern Spain where Lyme disease is endemic (14), and a low prevalence of infection was found (0.5%), but a new Borrelia sp. (Borrelia sp. strain R57), whose clinical and pathogenic importance remains unknown, was widely distributed among small mammals (12.5%). A limited number of small mammals from the same area was also analyzed for the presence of DNA of A. phagocytophilum, but all the specimens were negative (31). All these results were explained by the low number of Ixodes nymphs parasitizing small mammals in this area, with a 1:450 ratio of infestation of nymphs to that of larvae (14). The study area is particularly relevant due to the endemicity of Q fever pneumonia (29) and its proximity to an area where a new species of Rickettsia causing human disease, Rickettsia monacensis, has recently been identified in a patient (20a). However, no data are available regarding the presence of C. burnetii or Rickettsia spp. in small mammals in Spain. All these data create an interest in the search for potential reservoirs of such organisms.
PCR-based methods have become widely used as rapid and effective tools for the detection and identification of tick-borne pathogens in ticks and animal reservoirs. Increased sensitivity and specificity can be achieved by combining PCR with a specific hybridization by means of reverse line blot (RLB) hybridization, a macroarray that is able to identify mixed infections (39, 40). This study was undertaken to investigate the prevalence of tick-borne pathogens in domestic and wild small mammals in northern Spain. The main aim of the study was to determine the risk of disease in areas of potential contact between humans and small mammals carrying pathogens. In recreational areas, large numbers of human beings might come in contact with ticks and tick-borne pathogens from wildlife. Sheep farms, on the other hand, were selected since sheep are the most abundant livestock species in the area. Peridomestic small mammals were selected to investigate the role of these species as reservoirs of some tick-borne bacteria affecting sheep (C. burnetii and A. phagocytophilum) that might put at risk professionals living and working around farms. Rapid screening of a selection of bacteria infecting small-mammal tissues was carried out using multiplex PCR, followed by RLB hybridization using genus-specific or species-specific probes. Using this approach, we report herein the infection rates in small mammals for A. phagocytophilum, C. burnetii, spotted fever group (SFG) rickettsiae, B. burgdorferi sensu lato, and Borrelia sp. strain R57, with the purpose of providing an assessment of the role of small mammals as reservoir hosts for tick-borne bacteria.
| MATERIALS AND METHODS |
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Small mammals were captured between years 2000 and 2005 in two consecutive studies carried out at 15 different sites in the Basque Country. In the first study (study 1), carried out between April 2000 and November 2002, domestic and wild rodents were sampled in areas surrounding five sheep farms and in forested areas nearby. Study 2 started in September 2003 and finished in May 2005, and small mammals were captured in 10 recreational areas where, as previously described (4), the tick population was abundant.
After the authority's permission was obtained, Sherman traps (7.6 cm by 8.9 cm by 22.9 cm; Tallahassee, FL) and INRA traps (5 cm by 5 cm by 15 cm; BTS Mechanique, Besançon, France) were used for the live capture of rodents. Captures were carried out throughout the year, but mainly in the spring and autumn months. In study 1, 120 traps (20 Sherman traps placed inside sheep farms and 100 INRA traps placed outdoors) were set for two consecutive nights, and 100 INRA traps were set overnight in study 2. In study 1, moles were also captured using 25 pincer traps (Michel Touchard et Fils, Grainville Langannerie, France) per sampling. To compare the abundances of these animals between studies, the small-mammal abundance index (SAI) was calculated as follows: SAI = (SC x 100)/(T x N), where SC is the number of small mammals captured, T is the number of traps, and N is the number of nights.
Processing of small mammals.
Trapped animals were immediately transported to the laboratory and examined for attached ticks and other ectoparasites. Live captured rodents were anesthetized with ether and with ketamine hydrochloride (Imalgene 500; Merial, France) at a dose of 10 mg/kg of body weight intramuscularly and euthanized in a CO2 chamber. At necropsy, samples from different tissues were collected (ear, urinary bladder, spleen, liver, kidney, lung, and brain) and stored at –80°C. Small mammals were classified by external morphological data and skull features (1, 6, 32). Collected ticks were identified using taxonomic keys (15, 26).
DNA extraction and multiplex PCR.
DNA was extracted from pools of tissues and ear samples by using a QIAamp DNA mini kit (QIAGEN, Hilden, Germany), with a previous treatment with proteinase K for 3 h. A negative control was included for every 10 samples. The DNA concentration was determined for each sample with a NanoDrop ND-1000 spectrophotometer (NanoDrop Technologies, DE).
DNA was subjected to two multiplex PCR amplifications, one for the detection of C. burnetii and A. phagocytophilum and a second one for the detection of SFG rickettsiae and Borrelia spp. The oligonucleotide sequences of the primers, the gene targets, the concentration of each primer, and the annealing temperature of the PCR are shown in Table 1. Extracted DNA (100 to 200 ng) was used in each PCR.
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The prevention of cross-contamination and false-positive results was managed by using plugged tips, setting PCRs in a room separate from that used for DNA extraction, and including a negative (water) control in each run.
RLB hybridization.
To increase the detection limit of the PCR assay, PCR amplicons were hybridized to DNA probes specific for C. burnetii, A. phagocytophilum, Borrelia sp. strain R57, SFG rickettsiae, and Borrelia spp. by RLB hybridization. The probes, synthesized by MWG Biotech AG (Germany) with a C6 amino linker, were as listed in Table 1. The preparation of RLB membranes and hybridization were carried out as previously described by Gubbels et al. (17) with the following adaptations: the complete amplification reaction mixture (25 µl) was loaded onto the blotter after dilution with 2x SSPE-0.1% sodium dodecyl sulfate (1x SSPE is 0.18 NaCl, 10 mM NaH2PO4, and 1 mM EDTA [pH 7.7]) to a total volume of 160 µl, incubation was carried out at 48°C for 60 min, and washing steps were performed at 40°C. After hybridization, PCR products were stripped from the membrane as previously described by Gubbels et al. (17) and the membrane was rinsed and stored in 20 mM EDTA (pH 8.0) at 4°C until the next hybridization and reused a maximum of eight times.
To exclude false-positive results, negative controls included during DNA extraction and PCR amplification were also subjected to RLB hybridization. The specificities of the probes were tested against those of the previously constructed plasmids, which were also used as positive controls in each assay.
Identification of species of Borrelia.
Samples positive for Borrelia spp. by multiplex PCR (16S rRNA gene) and RLB hybridization were analyzed using a PCR specific for B. burgdorferi sensu lato, targeting the 5S-23S rRNA intergenic spacer, followed by RLB hybridization with specific probes described previously (13, 14, 39, 40) for B. burgdorferi sensu lato, B. burgdorferi sensu stricto, B. afzelii, B. garinii, B. valaisiana, and B. lusitaniae (Table 1). RLB hybridization was performed as previously described (14).
Statistical analysis.
The prevalence of each bacterial species was analyzed according to independent variables, such as host species, study (study 1 and study 2), and date of sampling (season and year), by chi-square or Fisher's exact test by using the SAS statistical package (version 8.0; SAS Institute Inc., Cary, NC). Significance was set at a P value of <0.05. Different logistic regression models including the same variables were performed on the data for the only agent (Borrelia sp. strain R57) that had a large enough set of positive results, and the model that better fitted the rates of infections was used.
| RESULTS |
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One hundred twenty-four of the 334 animals captured harbored at least one tick, with a maximum of 202 ticks observed in one A. sylvaticus mouse. The total amount of collected ticks was 1,961, accounting for 1,934 larvae (98.6%), 26 nymphs (1.3%), and one adult (an Ixodes acuminatus female). The percentage of small mammals parasitized and the number of ticks collected varied between studies, and the individual tick infestation followed a Poisson distribution. Whereas in study 1 the percentage of animals infested with ticks was low (9.1%), in study 2, 1,883 larvae were collected from 72.3% of the captured animals. Very few nymphs were found over the study periods, and all of them were collected in study 2 and consisted of 26 nymphs that were detached from 10 A. sylvaticus mice and one C. glareolus vole, giving a 1:72 average ratio of infestation of nymphs to that of larvae.
Ixodes ricinus was the most abundant tick species found, corresponding to 89.3% of larvae (100% in study 1 and 89.1% in study 2) and 96.2% of nymphs (all from study 2) collected. Three other species (Ixodes trianguliceps, Rhipicephalus turanicus, and Haemaphysalis concinna) were sporadically collected. I. ricinus larval infestation varied strongly among captured small mammal species. A. sylvaticus was the most parasitized species with 7.3 larvae/animal, followed by C. glareolus with 1.1 larvae/animal. Other small mammal species harbored very few larvae, i.e., Apodemus flavicollis with 0.7, Sorex coronatus with 0.5, and Crocidura russula with 0.2, whereas Mus domesticus and Talpa europaea had none.
Tick-borne bacterial infection in small mammals.
All the nucleotide probes designed for hybridization assays gave positive results with their corresponding positive controls and did not show any cross-reaction. The sensitivity of the hybridization assay was assessed by RLB hybridization processing serially diluted PCR products and was found to be 1 or 2 orders of magnitude higher than that calculated for the multiplex PCR only. The absolute limit of detection for the combined PCR and subsequent RLB hybridization procedures using gene clones as templates was between 6 and 60 gene molecules for the different multiplex PCR amplifications.
Pools of tissues from 253 animals (127 from study 1 and 126 from study 2), belonging to A. sylvaticus (162; 64%) and six other species, were subjected to the two multiplex PCRs described above and RLB hybridization. The prevalences of infection were different between animal species (Table 2). The most frequently infected species was C. glareolus, with 68.8% of the studied specimens (11/16) harboring DNA from some of the bacteria investigated, followed by A. sylvaticus (33.3%), C. russula (16.7%), S. coronatus (14.3%), and M. domesticus (10.7%). All the moles and A. flavicollis were negative, though only three specimens of the latter were examined. The prevalences were similar between studies (Table 2), with 26.0% of the analyzed animals being positive in study 1 and 30.1% in study 2.
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Two domestic mice (M. domesticus) captured in the spring and winter in 2000 in the premises of a sheep farm (study 1) had positive hybridization with the C. burnetii probe. The remaining captures of that period were negative for C. burnetii (seven A. sylvaticus mice, two C. glareolus voles, one A. flavicollis mouse, and one S. coronatus shrew). In the spring of 2001, one of the seven A. sylvaticus mice captured in a forest area near the same farm was also positive, whereas other small mammals trapped in this season (five M. domesticus mice and two C. glareolus voles) were negative. These results indicate that 28.6% of domestic mice (M. domesticus) and 7.1% of wood mice (A. sylvaticus) were infected in this farm. A. phagocytophilum was detected in one C. russula shrew captured in study 1 and one A. sylvaticus mouse from study 2, which represent 16.7% and 0.6% infection rates for these species, respectively, and an overall infection rate of 0.8%. Rickettsia was the only pathogen included in this study that was never detected in any of the small mammals tested. Coinfection with more than one pathogen was found in two small mammal species and accounted for 0.8% (2/253) of the animals analyzed (Table 2). The combinations were those formed by B. afzelii and Borrelia sp. strain R57 in one C. glareolus vole and by C. burnetii and Borrelia sp. strain R57 in one A. sylvaticus mouse.
| DISCUSSION |
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The mean number of I. ricinus larvae in A. sylvaticus in both studies (7.3) is clearly lower than in studies from Sweden (49.1) (42) but higher than in several European studies, e.g., 1.7 in Switzerland (25), 2.0 in La Rioja, Spain (11), and 2.1 in Ireland (16). In addition, few nymphs (26 nymphs) were collected, providing a 72:1 overall ratio of larvae to nymphs. This low nymphal infestation may limit the capacity of transmission of tick-borne bacteria to small mammals. This could be especially true when transovarial transmission of pathogens in ticks does not exist or occurs at a very low level and infection must be transmitted in the course of feeding by infected nymphs, as is the case for B. burgdorferi. However, the observed 72:1 ratio of larvae to nymphs was markedly lower than the one reported by Gil et al. (14) in the same region (450:1), but the prevalence of B. burgdorferi sensu lato in small mammals was higher (0.8% in study 1 and 1.6% in study 2) than in the former study (0.5%), suggesting an increase in nymphal infestation in recent years. Interestingly, this is the first report of B. afzelii infection of small mammals in Spain and the first time that S. coronatus has been involved as a reservoir of Lyme borreliosis. The prevalence values of B. afzelii infection found in S. coronatus (14.3%) and C. glareolus (6.3%) were markedly lower than those found in shrews and rodents in Central Europe (20, 22, 47). In any case, our results confirm reports by other groups that propose small mammals as reservoirs of B. afzelii (18, 19). Despite being the most abundant species captured and analyzed, none of the A. sylvaticus specimens was positive for B. burgdorferi sensu lato, suggesting its low contribution in the transmission of these spirochetes to subadult tick stages. These findings are in accordance with previous studies that found lower numbers of ticks and higher infection prevalences in bank voles than in Apodemus mice (23, 28). The absence of B. burgdorferi sensu stricto, B. garinii, and B. valaisiana in the analyzed small mammals contrasts with the results reported for questing ticks from the vegetation in our region, where B. burgdorferi sensu stricto, B. garinii, and B. valaisiana and not B. afzelii are the most prevalent genospecies (5, 10, 14). Hence, the main reservoir hosts for B. burgdorferi sensu lato in northern Spain remain unknown, and other mammal species, lizards, or birds may play a major role in the maintenance of this spirochete in the natural environment.
The novel Borrelia sp. strain R57, a spirochete closely related to the genus Borrelia but forming a clade separate from that of the Lyme disease agent and relapsing fever organisms (14), was widely distributed in rodents and shrews, both in sheep farms boundaries (22.1%) and in recreational parks (27.8%). Especially noteworthy were the detection of Borrelia sp. strain R57 in a domestic mouse and its high prevalence in bank voles (68.8%). These two species of small mammals and most of the animals captured in study 1 had low tick infestation levels, suggesting that Borrelia sp. strain R57 might be transmitted by ectoparasites other than ticks. This was already proposed by Gil et al. (14), who found that all the ticks collected from Borrelia sp. strain R57-positive small mammals were negative. The overall prevalence of Borrelia sp. strain R57 obtained in this study was two times higher than that previously reported by Gil et al. for regions in northern Spain where Lyme disease is endemic (14). The only methodological difference among both studies was probe concentration, which was much higher in the present study (16 versus 0.4 µM), thus increasing the sensitivity of the assay. Interestingly, Borrelia sp. strain R57 and B. afzelii, the only genospecies of B. burgdorferi found in northern Spain, were found as a mixed infection in a C. glareolus specimen, which suggests that an exclusion phenomenon does not exist between these two species, although the influence of such a possibility on the lack of distribution of other Borrelia genospecies should be further investigated.
In the United States, rodents are implicated as natural reservoirs for A. phagocytophilum (43). In Europe, this pathogen has been detected in several species of rodents such as A. flavicollis (25, 41), Apodemus agrarius, Rattus rattus (8), C. glareolus, A. sylvaticus (25), and shrews (Sorex araneus) (25), but their role as reservoirs is not clear. In our area, this agent has been associated with ovine and bovine abortions in several mountainous areas (12, 21) and in roe deer (31), but it was not detected among a small number of small mammals tested, probably due to the relatively low number of nymphs found to be infesting them (31). In the present study, we detected A. phagocytophilum in A. sylvaticus (0.6%) and C. russula (16.7%). Here, the relatively higher proportion of nymphs observed would explain the higher prevalence in a manner similar to that described above for B. burgdorferi. Also interesting was the detection of A. phagocytophilum in C. russula, since this is the first time that this shrew species has been involved as a possible reservoir. Nevertheless, the overall prevalence (0.8%) found in this study is clearly lower than in studies from Bulgaria (7.7%) (8) and Switzerland (8 to 10%) (25), where rodents seem to represent important reservoirs for this agent.
C. burnetii has a worldwide distribution, and many wild and domestic mammals (mainly sheep, cattle, and goats), birds, and arthropods, such as ticks, are considered their reservoirs. However, domestic ruminants represent the most frequent source of human infection. The disease occurs throughout Spain, and the incidence of its respiratory manifestations is especially high in our area (Basque Country) (29), where the largest series of Q fever pneumonia in Europe have been reported (27). Furthermore, this agent has a high importance as an abortifacient agent in sheep flocks in northern Spain (30). There are several serological studies that implicate small mammals in the wild and domestic cycles of Q fever (24, 38, 44), but very few studies demonstrate the presence of C. burnetii DNA in small mammals by molecular techniques (41). Therefore, the molecular detection of C. burnetii DNA in A. sylvaticus (0.6%) and M. domesticus (7.1%) captured in a sheep farm with previous reports of abortion (P. Gabiria, personal communication) is an interesting finding. These results suggest that mice would have acquired the infection by direct contact with infected sheep or with sheep fetuses or placentae inside the farm or in the pasture and that in the study region, C. burnetii developed in a peridomestic cycle rather than in a wild cycle and associated with infected flocks. Consequently, the risk of transmission to humans is associated mainly with domestic ruminants, and control and surveillance of C. burnetii in the animal reservoir environment are therefore needed to avoid human infection.
Ixodidae family ticks may act as vectors, reservoirs, and amplifiers of SFG rickettsiae (34), and small rodents have been shown to be susceptible to infection by several Rickettsia species (37). However, the DNA of the SFG rickettsiae was not detected in any of the animals analyzed in this study, suggesting that these animals are not involved as reservoirs of these pathogens in this area. This is in accordance with available data on the scarce number of Rickettsia-positive tick specimens in the same areas (J. F. Barandika, unpublished data) and with the low incidence of human rickettsiosis in the studied area (2).
In summary, a better knowledge of the wild and peridomestic cycles of tick-borne bacteria has been achieved and questions have been raised concerning the ecology of these zoonotic organisms. The complex cycle of these agents and the variations that could suffer over time suggest the need for continuous environmental surveillance to detect variations and prevent risks for transmission to humans.
| ACKNOWLEDGMENTS |
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We thank the EDEN Sixth Framework EU project (contract reference no. 010284-2) for providing resources for ongoing work and an expert tick and tick-borne disease forum for discussions.
| FOOTNOTES |
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Published ahead of print on 10 August 2007. ![]()
Present address: Hospital Universitario de Getafe, 28905 Getafe (Madrid), Spain. ![]()
| REFERENCES |
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