Associations of passerine birds, rabbits, and ticks with Borrelia miyamotoi and Borrelia andersonii in Michigan, U.S.A.
© Hamer et al.; licensee BioMed Central Ltd. 2012
Received: 29 August 2012
Accepted: 9 October 2012
Published: 11 October 2012
Wild birds contribute to maintenance and dissemination of vectors and microbes, including those that impact human, domestic animal, and wildlife health. Here we elucidate roles of wild passerine birds, eastern cottontail rabbits (Sylvilagus floridanus), and Ixodes dentatus ticks in enzootic cycles of two spirochetes, Borrelia miyamotoi and B. andersonii in a region of Michigan where the zoonotic pathogen B. burgdorferi co-circulates.
Over a four-year period, wild birds (n = 19,631) and rabbits (n = 20) were inspected for tick presence and ear tissue was obtained from rabbits. Samples were tested for Borrelia spirochetes using nested PCR of the 16S-23S rRNA intergenic spacer region (IGS) and bidirectional DNA sequencing. Natural xenodiagnosis was used to implicate wildlife reservoirs.
Ixodes dentatus, a tick that specializes on birds and rabbits and rarely bites humans, was the most common tick found, comprising 86.5% of the 12,432 ticks collected in the study. The relapsing fever group spirochete B. miyamotoi was documented for the first time in ticks removed from wild birds (0.7% minimum infection prevalence; MIP, in I. dentatus), and included two IGS strains. The majority of B. miyamotoi-positive ticks were removed from Northern Cardinals (Cardinalis cardinalis). Borrelia andersonii infected ticks removed from birds (1.6% MIP), ticks removed from rabbits (5.3% MIP), and rabbit ear biopsies (5%) comprised twelve novel IGS strains. Six species of wild birds were implicated as reservoirs for B. andersonii. Frequency of I. dentatus larval and nymphal co-feeding on birds was ten times greater than expected by chance. The relatively well-studied ecology of I. scapularis and the Lyme disease pathogen provides a context for understanding how the phenology of bird ticks may impact B. miyamotoi and B. andersonii prevalence and host associations.
Given the current invasion of I. scapularis, a human biting species that serves as a bridge vector for Borrelia spirochetes, human exposure to B. miyamotoi and B. andersonii in this region may increase. The presence of these spirochetes underscores the ecological complexity within which Borrelia organisms are maintained and the need for diagnostic tests to differentiate among these organisms.
KeywordsTicks Borrelia miyamotoi Borrelia andersonii Ixodes Wild birds Eastern cottontail rabbit Relapsing fever Lyme disease
When considering the ecology of tick-borne diseases, it is becoming increasingly clear that wild birds maintain and move ticks and pathogens by serving as blood meal hosts and pathogen reservoirs. Birds have been implicated as reservoirs for several spirochetes within the genus Borrelia worldwide[1–5] and as vehicles for the long-distance dispersal of Borrelia spirochetes and ticks through their migratory movements[5–10]. For example, the phylogeographic structure of populations of three Borrelia species is congruent with vagility of vertebrate hosts, such that strains of the bird-associated B. garinii and B. valaisiana are spatially-mixed across countries, whereas strains of the rodent-associated B. afzelii are comparatively more differentiated geographically.
Borrelia spirochetes comprise three distinct species groups: (i) the Lyme borreliosis group, transmitted by hard ticks, which includes the agents of human Lyme disease such as B. burgdorferi, B. afzelii, and B. garinii as well as species not known to be pathogenic such as B. andersonii; (ii) the relapsing fever group, largely transmitted by soft ticks, which includes agents of human relapsing fever such as B. duttonii and B. hermsii; and (iii) a group that is most similar by molecular phylogenetic analysis to the relapsing fever spirochetes, but which are associated with hard tick vectors, including B. theileri, B. lonestari, and B. miyamotoi.
Borrelia miyamotoi is a relapsing fever group spirochete that was originally described in I. persulcatus in Japan and later in I. scapularis in North America. In North America, B. miyamotoi has been detected in the white-footed mouse Peromyscus leucopus[12, 15, 16] and wild turkey Meleagris gallopavo. Given the apparent cosmopolitan association of B. miyamotoi within populations of human-biting Ixodes spp. ticks throughout North America and Europe, it is likely that humans are regularly exposed, albeit the B. miyamotoi infection prevalence (1.7-3.4% in adults and nymphs) is typically an order of magnitude less than that of B. burgdorferi infection prevalence in the same tick populations[12, 18–22]. B. miyamotoi has recently been associated with relapsing fever and Lyme disease-like symptoms in humans in Russia, and has been found in ticks removed from humans in other countries. Due to diagnostic testing specific for Lyme borreliosis group spirochetes, undetected human infection with B. miyamotoi in cases of Lyme disease-like illness is a possibility in North America and Europe.
Borrelia andersonii is a Lyme borreliosis group spirochete that was designated as a new species in 1995 subsequent to its initial classification as an antigenic variant of B. burgdorferi[25, 26]. Borrelia andersonii has not been implicated in human disease, which may reflect its association with I. dentatus - a tick that feeds almost exclusively on birds and rabbits. Although direct human-biting by I. dentatus is rare, it has been documented several times across the I. dentatus range[28–34], and B. andersonii has been detected in an I. dentatus tick removed from a human in Connecticut. Furthermore, B. andersonii was detected in a questing I. scapularis nymph and in ear tissue of a white-footed mouse; these observations suggest that I. scapularis may serve as a bridge vector of this spirochete to humans.
We recently identified a focal cryptic cycle of B. burgdorferi transmission maintained by several species of wild birds, eastern cottontail rabbits, and Ixodes dentatus ticks- a species that feeds almost exclusively on birds and rabbits and postulated that on-going range expansions of the bridge vector I. scapularis into such zones of cryptic pathogen maintenance could result in increased risk of human exposure. In this study, our objectives were to determine prevalence, host and vector associations, and phenology of other Borrelia species of potential public health importance, including B. miyamotoi and B. andersonii, that may be co-circulating within avian host and cryptic vector populations. We hypothesized that the phenology of bird-associated ticks would help to explain the observed patterns of pathogen prevalence.
Borrelia species detection and nucleotide sequencing
Ticks were identified to species and stage using published keys[27, 38]. Total DNA was extracted using the DNeasy Blood and Tissue Kit (Qiagen, Valencia, CA) as described in Hamer et al.. Ear biopsies and nymphs were extracted individually, and conspecific larvae from the same individual animal were pooled for extraction. To confirm morphological identification, a subset of ticks were subjected to PCR and sequencing of the 5.8S rRNA – 28S rRNA gene internally transcribed spacer (ITS-2). The B. burgdorferi strain B31-infected nymphal I. scapularis acquired from the Centers for Disease Control and Prevention served as the positive controls. Borrelia spp. were detected using a nested polymerase chain reaction (PCR) for the 16S–23S rRNA intergenic spacer region (IGS) of Borrelia spp.. PCR fragment sizes are approximately 1000 bp for B. andersonii and B. burgdorferi, and 500 bp for B. miyamotoi. Amplicons from positive reactions were purified (Qiagen, Valencia, CA) and subjected to direct DNA sequencing. Sequences were determined in both directions using an ABI Prism 3100 Genetic Analyzer (Applied Biosystems, Foster City, CA), and were compared to published sequences using the basic local alignment search tool in GenBank.
Chi-squared tests for independence were used to assess frequency of coinfestations. Logistic regression was used to assess tick infection over time. Minimum infection prevalence (MIP; i.e., assuming one positive larva per positive pool) was used for tests conducted on pooled larvae. The evolutionary history among strains within a Borrelia species was inferred using a neighbor-joining method in Mega5 in which the evolutionary distances were computed using the maximum composite likelihood method and are in the units of the number of base substitutions per site. Novel strain sequences were deposited [GenBank:HMO15226-HMO152237 for B. andersonii; GU993309 for B. miyamotoi. The effect of sample size on strain richness was assessed using a web-based rarefaction calculator (University of Alberta, Edmonton, Canada; available athttp://www.biology.ualberta.ca/jbrzusto/rarefact.php). Strain richness was estimated by using the nonparametric model of Chao-1, which considers the number of operational taxonomic units observed, and the frequency with which each was observed, to estimate total population strain richness.
A total of 12,301 ticks was removed from 19,631 bird captures (10.6% infestation prevalence) of which 86.4% were I. dentatus, 13.4% were Haemaphysalis leporispalustris, and <1% were I. scapularis and Dermacentor variabilis. Among the 105 avian species investigated, the bird species most commonly parasitized by ticks included Brown Thrasher (Toxostoma rufum), Lincoln’s Sparrow (Melospiza lincolnii), White-throated Sparrow (Zonotrichia albicollis), Eastern Towhee (Pipilo erythrophthalmus), Eastern White-crowned Sparrow (Zonotrichia l. leucophrys), Carolina Wren (Thryothorus ludovicianus), Song Sparrow (Melospiza melodia), Hermit Thrush (Catharus guttatus), American Robin (Turdus migratorius) and Fox Sparrow (Passerella iliaca). A total of 131 ticks was removed from 20 captures of eastern cottontails (75% infestation prevalence). The two most common tick species on cottontails were I. dentatus and H. leporispalustris, which parasitized 65 and 25% of captures, respectively. The PCR of the tick ITS-2 region resulted in molecular confirmation of the morphological identification for the subset of ticks that were tested (n = 17 which included representatives of all four tick species found on birds and rabbits).
Phenology of bird-associated ticks
Detection and diversity of B. miyamotoi
Borrelia species infection prevalence in ticks and ear biopsies
Ticks from birds
Ticks from rabbits
Rabbit ear biopsies
Detection and diversity of B. andersonii
Borrelia andersonii infection was found in ticks removed from birds and rabbits and rabbit ear tissue. Regarding bird ticks, 35 of 2220 samples (1.6%) were PCR-positive with sequences identical to or with significant sequence homology to B. andersonii (Table1); positive samples included I. dentatus (n = 30 samples), H. leporispalustris (4 samples), and I. scapularis (1 sample). Additionally, 18 samples were PCR-positive for Borrelia species with an IGS fragment at the expected size for B. burgdorferi or B. andersonii, but no sequences were obtained from these samples. As such, the reported tick infection prevalences are considered as a minimum.
The prevalence in nymphs was significantly greater than that of larval pools (6.2 and 0.5%, respectively; P < 0.0001). Positive samples were collected in all four years of the study, and annual variation in tick infection prevalence was not significant (R2 = 0.23; P = 1). Aggregating years, the highest monthly prevalence of 5.5 – 5.8% occurred in May and June, coinciding with peak I. dentatus nymphal phenology and the first larval activity peak, and prevalence significantly decreased over the season (R2 = 0.43; P < 0.0001). From mid-June through mid-August—a period that largely excludes the spring and fall migrations in our area—we detected 12 B. andersonii-positive ticks/pools, comprising 34.3% of all positives. Of these mid-summer positive samples, 10 (83.3%) were from hatch-year birds, indicative of local exposure. The 35 B. andersonii-positive samples were removed from 29 individual birds of 12 species. From the perspective of natural xenodiagnoses (i.e., identifying reservoir-competent host species based on production of infected larvae, in the absence of simultaneously attached infected nymphs), these results implicate six avian species as reservoir competent for B. andersonii: Brown Thrasher, Connecticut Warbler, Gray Catbird, Hermit Thrush, Swamp Sparrow, and Tufted Titmouse. Three individual birds were associated with more than one B. andersonii-positive sample collected either simultaneously or in a sequential capture.
Of the ticks removed from 20 rabbit captures, 5 of 120 (4.2%) adult and 2 of 2 (100%) nymphal I. dentatus were confirmed by sequencing as positive for B. andersonii (Table1); positive ticks came from 4 individual rabbits. None of the 7 adult or 2 nymphal H. leporispalstris tested positive for Borrelia species. Of the 20 rabbit ear biopsies, 1 (5%) was confirmed by sequencing as positive for B. andersonii (Table1). Additionally, 4 I. dentatus samples and 2 rabbit ear biopsies were PCR-positive for Borrelia species with an IGS fragment at the expected size for B. burgdorferi or B. andersonii (~1000bp), but no sequences were obtained from these samples. As such, the reported tick infection prevalences are considered as a minimum.
Drawing upon current understanding of the ecology of B. burgdorferi and B. miyamotoi, within the context of I. scapularis phenologies in the eastern U.S., we can extrapolate cautiously to interpret and better understand the results found here regarding B. andersonii and B. miyamotoi infections in I. dentatus ticks attached to passerine birds in the Upper Midwestern U.S. Transovarial transmission for B. burgdorferi is not known to occur in I. scapularis, and thus, larvae hatch uninfected. Larvae and nymphs become infected horizontally by feeding on infected hosts, resulting in infected nymphs and adults. The infection prevalence in questing adults is usually double that of questing nymphs in a given area and in part is attributed to each tick having two opportunities of becoming infected. If B. andersonii is similar to B. burgdorferi in that transovarial transmission does not occur, then through implementation of natural xenodiagnosis our study implicates six avian species as competent reservoirs for B. andersonii; the presumption is that infected larval ticks obtained their spirochete infections from the birds upon which they were feeding at the time the sample was taken. B. miyamotoi, on the other hand, is transovarially transmitted in I. scapularis, and little is known about the contribution of any reservoir species to its persistence via horizontal transmission. Thus, in addition to nymphs and adult ticks being infected, questing larvae can be infected as well. Little data exist on the infection prevalence of questing larvae, but in general, the infection prevalences of questing nymphs and adults are low and are similar[12, 18], suggesting that very little horizontal transmission occurs. While the reservoir competency of birds for B. miyamotoi using our study data cannot be established due to the potential for transovarial transmission, we suggest that I. dentatus tick and Northern Cardinals in particular may be important in the life history of B. miyamotoi due to the significant proportion of infected ticks contributed by this host species relative to its role in feeding ticks.
Tick phenology has implications for Borrelia species maintenance and infection dynamics of hosts. In eastern U.S. peak nymphal activity occurs in late spring/early summer. In the Northeast, there is a small peak of larval activity in late spring/early summer, but the main peak is in late summer[49–51]. This asynchronous sequence of nymphs host-seeking prior to larvae allows for hosts to become infected by nymphs, and then to serve as a source of infection to larvae later in the season and is believed to be a driving force in the high nymphal infection prevalence. Given the different modes of transmission between pathogens, in the Northeast peak B. burgdorferi transmission to hosts occurs in early summer, correlating with nymphal activity period, whereas peak B. miyamotoi transmission occurs in late summer, correlating with peak larval activity period. The tick phenology is different in the northern Midwest, however, where the late spring/early summer larval activity period is often the main peak, coincident with the nymphal activity peak[37, 48]. The more synchronous activity periods of nymphs and larvae is believed to results in some larvae feeding on hosts that have not yet been infected by nymphs, and therefore may contribute to lower nymphal infection prevalence in the Midwest compared to the Northeast. The synchronous phenology in the Midwest, however, may provide increased opportunities for co-feeding transmission, but presently its contribution is unknown.
In our study, we found that larval I. dentatus exhibited bimodal activity peaks in late spring/early summer and again in the fall, with nymphs active in the spring though mid-summer, similar to previous reports[52–54]. In the same way that I. scapularis nymphal activity prior to larval activity supports B. burgdorferi maintenance, the phenology we detected for I. dentatus is likely to support not only the low-level B. andersonii infection we report herein, but also our earlier findings of B. burgdorferi in the same ticks. However, because larval activity was bimodal with the first larval peak coincident with nymphal activity, pathogen prevalence may be reduced relative to what would be expected if the activity of the two life stages were completely asynchronous. As a potential to further augment pathogen prevalence in ticks, we suggest the concept of co-feeding transmission in this system requires further attention, since significant frequencies of simultaneous co-infestations of the same avian hosts with both nymphs and larvae occurred. For example, we detected a Song Sparrow that simultaneously harbored B. andersonii-infected nymphs and larvae. The infection prevalence of I. dentatus adults attached to rabbits interestingly was lower/not significantly different from the infection prevalence of nymphs attached to birds; this contradicts the increasing pattern of B. burgdorferi infection in nymphs and adults of I. scapularis. This may suggest that B. andersonii transmission dynamics to I. dentatus nymphs differs from that of B. burgdorferi transmission dynamics to I. scapularis nymphs. Alternatively, the actual infection prevalence of B. andersonii in adult I. dentatus may have been higher, as there were four other Borrelia-positive ticks for which we do not know the species identity.
In contrast, the seasonal activity of nymphs relative to larvae may be less important for the maintenance of B. miyamotoi given the likely occurrence of transovarial transmission in I. dentatus. In addition to I. scapularis, B. miyamotoi has been found to be transovarially transmitted in I. pacificus, I. ricinus, and I. persulcatus. A majority of B. miyamotoi-infected ticks in our study were larvae removed from birds in the fall, a pattern that parallels the finding in which B. miyamotoi infection in mouse hosts rose toward the end of the summer coincident with the larval phenology. A majority of B. miyamotoi-infected ticks occurred on Northern Cardinals, which are permanent residents in Michigan that typically stay within 8 km of where they were hatched, thereby demonstrating local acquisition of the spirochete. The presence of B. miyamotoi-infected ticks on two Hermit Thrushes, which do not breed in the area, affords a mechanism for migratory importation of the spirochete. Interestingly, we did not find any adult I. dentatus infected with B. miyamotoi, but given the low infection prevalence found in nymphs (0.7%) and the number of I. dentatus found on rabbits (n=120), there might not have been enough power to detect an infected tick.
The phenologies of I. dentatus and H. leporispalustris were strikingly opposite; this pattern is not explained by associations of the tick species with spring and fall migrants versus local/breeding birds, respectively. We therefore used H. leporispalustris as a bioassay or sentinel tick species to increase our ability to detect Borrelia spp. among birds across a broader temporal period and in a greater number of samples than would have been afforded by assessment of only I. dentatus, a known Borrelia spp. vector. Indeed four of the 480 H. leporispalustris pools removed from birds were infected with B. andersonii, though the ability of H. leporispalustris to transmit these agents remains unknown.
A high level of genetic diversity of B. andersonii was present within birds, rabbits, and their ticks at this focal site, with twelve unique IGS strains present within 33 sequenced samples derived from ticks removed from 11 host species. This strain richness, when standardized by sample size, is similar to what we reported previously for B. burgdorferi in the same samples (25 IGS strains present within 72 sequenced samples). However, whereas the statistical analysis indicated that the sampling in this study captured most of the B. andersonii strains estimated to be present in the system, this was not true for B. burgdorferi, where strain richness was estimated to be an order of magnitude higher than what we detected. Furthermore, in comparing the amount of evolutionary distance that separates the B. andersonii strains to that which separates the B. burgdorferi found within the same samples, we found that the former is much greater (0.02 nucleotide substitutions per site) than the latter (0.005 nucleotide substitutions per site on aphylogram assuming the same model of evolution as above). These data suggest that the duration of establishment of B. andersonii may be greater than that of B. burgdorferi. In this study location, where I. scapularis is not endemic, differences in diversity between B. burgdorferi and B. andersonii is not likely explained by adaptation to another tick, but may relate to differences in host range and differences in contributions by migratory birds, transmission efficiency, or other unmeasured factors.
At the other end of the spectrum, all but one of the 12 bird-associated B. miyamotoi sequences were identical at the IGS locus to ‘Type 4’ that has been reported previously from I. scapularis nymphs in Connecticut and from wild turkey (Meleagris gallopavo) tissue and blood in Tennessee. The novel Michigan variant had a single nucleotide polymorphism from Type 4, and was different from two mammal-associated variants we previously reported from the ear tissue of a white-footed mouse (Peromyscus leucopus) and an eastern chipmunk (Tamias striatus) collected at different sites in Michigan (Figure3). This low diversity of B. miyamotoi agrees with what has been found previously in I. scapularis, I. ricinus, I. pacificus, and I persulcatus (for example[18, 44, 56]).
Comparison of our current results with our previous report of a minimum of 3.5, 3.1, and 20% B. burgdorferi infection prevalence in these bird ticks, rabbit ticks, and rabbit ears, respectively, confirms that individual mammals and birds are exposed to more than one Borrelia species. For instance, we amplified B. andersonii from the ear tissue of a rabbit that concurrently harbored B. burgdorferi- infected I. dentatus, and rabbits infected with B. burgdorferi harbored B. andersonii-infected ticks. We captured at least three birds that concurrently harbored ticks infected with B. andersonii and B. burgdorferi, and one bird that concurrently harbored ticks infected with B. miyamotoi and B. burgdorferi. Co-infections of I. scapularis with B. burgdorferi and B. miyamotoi has been reported previously: Barbour et al. found that the frequency of co-infections in 7,205 questing nymphs from across the northern U.S. was not different than expected; Ullmann et al. detected no coinfection in 250 I. scapularis nymphs from New Jersey, and Tokarz et al. found that all 7 B. miyamotoi-infected adult I. scapularis in a sample of 286 from New York were co-infected with B. burgdorferi. The ecological and epidemiologic significance of co-infections with two or more Borrelia species requires additional study.
Wild birds and ticks that specialize on birds and rabbits are involved in the natural maintenance and transmission of B. miyamotoi and B. andersonii, two spirochetes of potential public health importance. Understanding the ecology of cryptic vector species is of public health importance because they may augment the pathogen load in the environment that is a source of infection to sympatric bridge vectors, and furthermore may extend the time that reservoirs are infected and thereby allow more opportunity for transmission to bridge vectors. Given continued range expansions of I. scapularis from many endemic foci[58, 59], including near our study region in Michigan, it is likely that humans will be exposed to these cryptic microbes with unknown health consequences. There has been a linear increase in the number of published genospecies of the B. burgdorferi sensu lato complex with 1–3 new species described per year since 1992, and our understanding of the clinical significance of the various members of the complex is continuing to evolve. Studies of natural spirochete hosts and vectors may provide key information for understanding emerging human risk, as has been the case in the recognition of B. bissettii as a causative agent of human disease in Europe. The co-occurrence of three Borrelia species within a host community and vector population highlights the need for diagnostic assays that can differentiate among these species for research, medical surveillance, and treatment.
Minimum infection prevalence
Internally transcribed spacer
Intergenic spacer region
Polymerase chain reaction.
We are grateful to Gabriel Hamer, Brenda Keith, Emily Koppel, Todd Lickfett, Aubrey Rankin, and Michelle Rosen for assistance in the field and laboratory. This work was supported by start-up funds to JIT and GJH and a Doctoral Dissertation Improvement Grant DEB-0910025 from the National Science Foundation to SAH.
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