Abstract
The GenBank/EMBL/DDBJ accession number of the complete nucleotide sequence of the Myotis polyomavirus and deduced amino acid sequence is FJ188392.
Three supplementary tables showing primer sequences, background information on bat specimens and GenBank accession numbers of the sequences analysed in this study are available with the online version of this paper.
Increased human development in wilderness areas of Canada and encroachment into bat habitats could lead to similar inter-species transmission of potentially zoonotic viruses that may be present in bats, particularly via species which can roost in human-made structures. Additionally, widespread mortality of the so-called migratory tree bats, that has now been documented at industrial-scale wind energy facilities throughout North America (Arnett et al., 2008; Baerwald et al., 2008; Betts, 1998) has created the potential for direct virus transmission between formerly cryptic forest bat species and domestic pets or livestock and indirect transmission to wildlife species which scavenge bat carcasses at wind turbines (e.g. foxes, skunks and crows; Klug & Barclay, 2008). Identification of such viruses and characterization of their biology and epizootiology would be invaluable in anticipating and possibly preventing transmission to humans or, if it occurred, in controlling its spread and impact.
At least 17 species of bats have been detected in Canada. These include little brown bat (Myotis lucifugus), Yuma myotis (M. yumanensis), long-legged myotis (M. volans), fringed myotis (M. thysanodes), northern myotis (M. septentrionalis), eastern small-footed myotis (M. leibii), Keen's myotis (M. keenii), long-eared myotis (M. evotis), western small-footed myotis (M. ciliolabrum), California myotis (M. californicus), big brown bat (Eptesicus fuscus), silver-haired bat [Lasionycteris (L.) noctivagans], hoary bat [Lasiurus (Las.) cinereus], red bat (Las. borealis), tri-coloured bat (formerly the eastern pipstrelle, Perimyotis subflavus), spotted bat (Euderma maculatum) and Townsend's big-eared bat (Corynorhinus townsendii). Of these species, the little brown bat, silver-haired bat, hoary bat, northern myotis, big brown bat and eastern red bat have been observed in the province of Manitoba (details in Bilecki, 2003). During winter in Manitoba, the little and big brown bats and northern myotis bats hibernate, while the three other local species, the migratory tree bats (silver-haired bat, hoary bat and eastern red bat), migrate south. The little brown and northern myotis bats hibernate in caves in the extensive limestone karst in the inter-lake and northern regions of Manitoba. Big brown bat hibernacula have not as-yet been identified. The little brown bats congregate at the caves in mid-August to late September, presumably to mate. Later in the year, they move to the caves where they habitually hibernate during winter. The bats leave the caves in mid-May to early June and females form maternity colonies in tree hollows and other structures, including buildings. Little brown bats, in particular, are common inhabitants of buildings throughout their range and are, therefore, the species most likely to be encountered by humans in Manitoba. In contrast, two of the three migratory tree bats (hoary and eastern red bats) have rarely been encountered by people historically, because they roost exclusively in the foliage of trees (Willis & Brigham, 2005). The third migratory species (the silver-haired bat) is also considered a tree-roosting species (Betts, 1998) but has been more often encountered by people when roosting in deadfall or woodpiles
If bats indeed harbour viruses that have the potential to cause severe disease in humans and other domestic animals, and if climatic and socio-economic changes are likely to lead to conditions that facilitate contact between bats and domestic animals, it might be useful to identify viruses that infect bats. Such surveys have been conducted elsewhere in the world with the identification of several previously unknown bat viruses. Because of the devastating effect of SARS on the economy of several countries, most of these studies have specifically targeted coronaviruses (Carrington et al., 2008; Chu et al., 2006, Dominguez et al., 2007; Gloza-Rausch et al., 2008; Lau et al., 2005; Poon et al., 2005). Our objective in this study was to carry out a preliminary screen of bats in Canada for the presence of viruses of several families. We attempted to isolate viruses from fresh tissue samples taken from trapped bats in cultured cells of bat, primate, rodent, porcine, ovine and avian origin. We also screened nucleic acids purified from these samples by PCR using low-specificity primers designed to amplify nucleic acids from all members of certain families of viruses. We detected RNA related to that of Rocky Mountain bat coronavirus (RMBCV) from little brown bats and DNA of a previously undescribed polyomavirus from female little brown bats and California myotis.
Bats.Bats for the study were obtained from three sources.
(i) Little brown bats were trapped using a harp trap set up at a cave in northern Manitoba during a September 2007 mating swarm. Some hibernating bats were also collected from hibernacula in two other caves in May 2008. Bats were euthanized on site by an overdose of inhaled isoflurane (Aerrane) and placed on ice for transport to the National Microbiology Laboratory (NML) in Winnipeg. Bats were processed for virus isolation within 48 h of collection. A Wildlife Scientific Permit (WB 06638) to trap the bats was obtained from the Wildlife and Ecosystem Protection Branch of Manitoba Conservation. The bats were treated in accordance with procedures approved by the Animal Care Committee of the Canadian Science Centre for Human and Animal Health (H-07-001 Rev.1). All individuals handling bats had been immunized against rabies and, according to recent tests, had antibody levels considered protective.
(ii) The Centre of Expertise for Rabies at the Canadian Food Inspection Agency (CFIA) provided bats diagnosed as negative for rabies. These bats had been submitted to the CFIA laboratories in Lethbridge, Alberta and Ottawa, Ontario, and frozen at –20 °C after diagnosis. This group of bats included little and big brown bats, silver-haired bats, hoary bats, Yuma myotis and California myotis.
(iii) Dead bats were collected for a survey of bat mortality at a Manitoba wind farm. These included silver-haired, hoary and red bats.
Sampling tissues.
All bats were processed in biosecurity level 3 facilities at either the NML or the CFIA Fallowfield laboratory in Ottawa. Carcasses were sprayed with 70 % ethanol and placed on absorbent paper for 5 min before dissection. One kidney and spleen, and portions of liver, lung, small intestine and brain were removed from each bat. All tissues from each live-trapped bat were pooled. For bats obtained from CFIA and the wind farm, tissues from up to four bats of the same species were pooled. BA [Medium 199 (Gibco), 50 mM Tris/HCl, pH 7.6, 1 % BSA and penicillin–streptomycin (Gibco)] was added to tissues from individual animals (2 ml) and pooled tissues (4 ml) and the tissues were homogenized either in a Polytron homogenizer or by shaking with a sterile ball bearing in a Retsch M300 oscillating homogenizer. The samples were then centrifuged at 16 000 g for 5 min and the supernatant was transferred to a fresh tube.
Inoculation of cultured cells.
Lamb and pig kidney cells, baby hamster kidney cells (BHK-21), chicken fibroblasts and quail fibroblasts (QT-35) were obtained from Marta Sabara (CFIA) and mouse fibroblasts (NIH-3T3), African green monkey (Vero) cells and bat tracheal (BT) cells were obtained from James Strong (Public Health Agency of Canada, NML). All cells were grown in medium normally used to propagate the cells.
Tissue homogenates were diluted 1/10 and 1/100 in BA and 100 µl of undiluted or diluted homogenate was added to cultured cells in 24-well culture dishes. After incubating for 1 h at 37 °C, the inocula were removed and replaced with 1 ml medium containing 5 % fetal bovine serum. Cells were observed for cytopathic effect (CPE) every 2 days. Any morphological differences or differences in the colour of the growth medium from mock-infected cells were considered a CPE. After 3 days of incubation, cultures inoculated with the lowest dilution of homogenate that contained viable cells were dispersed by trypsinization and re-plated. Inoculated cells were passaged in this manner five times and were discarded if no obvious CPE was observed. Samples from supernatants from cultures that showed CPE were transferred to electron microscope grids and screened for virus particles by the NML electron microscopy laboratory.
Extraction of nucleic acids.
Total nucleic acids were extracted from 140 µl tissue homogenate using the QIAamp viral RNA mini kit (Qiagen) following the manufacturer's instructions [this kit purifies viral DNA as well as RNA (Allan Grolla, personal communication)]. An additional washing step with buffer AW1 (Qiagen) was included. Before extraction, all samples were seeded with bacteriophage MS2 RNA as an internal control. Nucleic acid samples for PCR for DNA viruses and for the two-step real-time PCR for West Nile virus were used directly. For PCR for RNA viruses, RNA was converted to cDNA using the Qiagen Sensiscript RT kit with random nonamers (Gene Link) as primers. Control RNA from Hendra, Nipah, measles, SARS corona and rabies viruses were obtained from NML laboratories.
PCR.
The primer sequences used for PCR and RT-PCR are provided in Supplementary Table S1 (available in JGV Online). PCRs for corona, lyssa, flavi, bunya, Cache Valley and morbilli viruses were performed with ABS AmpliTaq (Applied Biosystems) according to the manufacturer's instructions. The amplification process included holding the samples at 94 °C for 15 min; 18 touch down cycles of 94 °C for 15 s, 55–37 °C (with a 1 °C decrease in temperature per cycle) and 72 °C for 30 s; 30 cycles of 94 °C for 15 s, 55 °C for 30 s and 72 °C for 30 s; 72 °C for 7 min. Secondary amplifications for corona, lyssa and morbilli viruses were performed on 1 µl of the primary PCR product using the same amplification conditions. PCR products were analysed by electrophoresis on 2 % agarose gels. In some gels, PCR products from control viral cDNAs were included. PCR products of the expected size were submitted to the NML genomics core facility and sequences were analysed by BLAST to determine if they resembled known viral sequences. Bacteriophage MS2 RNA, seeded into raw samples as a control for RNA extraction, was detected using quantitative RT-PCR (Dreier et al., 2005) by the virology facility at the NML.
Broad spectrum PCR for polyomavirus detected a conserved portion of the VP1 and VP3 genes (Johne et al., 2005). The remainder of the genome of polyomaviruses from three bats was obtained by long-range PCR using primers facing outwards from the initial product of the VP1 gene. The larger PCR product was cloned into pCRTOPO using a PCR cloning kit (Invitrogen). The sequence of the fragment was determined using primers bracketing the cloning site of pCRTOPO and additional primers were designed as sequencing progressed. Sequences were aligned into contigs using DNASTAR and represented complete sequences of both DNA strands. Open reading frames (ORFs) were deduced using MacVector 7. Deduced amino acid sequences of the Myotis polyomavirus genes for Large T-antigen, Small t-antigen, VP1 and VP2,3 were compared with those of other polyomaviruses using the PHYLIP 3.63 package. The complete nucleotide sequence of the Myotis polyomavirus and deduced amino acid sequences of the deduced proteins were submitted to GenBank and assigned the accession number FJ188392.
We attempted to detect viruses in Canadian bats by using two complementary strategies: to isolate virus in a variety of cultured cells and to screen samples by PCR using primers designed to amplify nucleic acids from members of selected families and genera of viruses and from individual viruses. The target viral families and genera were selected either because of a precedent for members spilling over into humans or because the tests were available in our laboratory, thus allowing us to undertake a broad generalized screening. In positive control reactions, the primers detected nucleic acids from representative target viruses.Live-trapped M. lucifugus
We examined 31 live-trapped M. lucifugus (Table 1). Twenty-one bats were collected from a mating swarm in September 2007. Of these, thirteen were female and seven were male (one unknown). An additional five bats were collected from each of two cave hibernacula in May 2008. All of these bats were male. Various tissues from individual bats were pooled and attempts were made to isolate virus using cultured cells. However, we observed no virus particles by electron microscopy, even after repeated attempts to detect virus in tissue culture supernatants and concentrated material. We did, however, detect virus infection by PCR analysis of nucleic acids purified from tissue homogenates of seven of the 31 live-trapped M. lucifugus examined (Table 1). We determined the nucleotide sequence of the PCR products, which confirmed that four of the viruses were polyomavirus while three were coronavirus. All four bats from which we detected polyomavirus were females.
Table 1. Virus nucleic acids detected in live-trapped M. lucifugus NVD, No virus was detected.
Bats from the Centre for Expertise in Rabies and bats collected from a wind energy facility
The Centre for Expertise in Rabies provided 84 bat carcasses representing four genera and six species (Supplementary Table S2, available in JGV Online). These bats were submitted to the Centre for Rabies Testing and were found to be negative for rabies virus. The carcasses, which had been stored frozen at –20 °C, were thawed overnight at room temperature before dissection. We detected polyomavirus in a pool from two female M. californicus bats submitted to the Centre from British Columbia. We also obtained 15 bat carcasses representing the three migrating species (Las. cinereus, L. noctivagans and Las. borealis) from a wind plant near Winnipeg. The carcasses were collected in autumn 2007 and frozen at –20 °C until the tissues were analysed by PCR. An additional Las. cinerus bat was submitted by a local veterinarian. No viruses were detected in these animals (total of 100).
Myotis polyomavirus
Polyomavirus DNA was detected using primers designed from a conserved portion of the VP1 gene of polyomaviruses. Using primers designed from the nucleotide sequence of the VP1 fragment, we amplified the remainder of the viral genome from three bats. The sequence of the entire genome was determined and putative ORFs for major polyomavirus proteins (VP1, VP2 and 3, Large T antigen and Small t-antigen) were deduced. The derived amino acid sequences for these proteins were compared with those of all other known polyomaviruses. Only VP1 sequences were available for the goose polyomavirus.
Fig. 1 depicts phylogenetic trees of the polyomavirus viral proteins based on a parsimony analysis of the amino acid sequences of the proteins. While there were some variations in the groupings when the sequences of the different proteins were compared, all four proteins of the Myotis bat virus were closely related to those of the mouse pneumotropic (Kilham) and squirrel monkey viruses.
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Myotis coronavirus
We amplified a 500 bp segment of RNA from a coronavirus in three M. lucifugus bats using primers designed to amplify a portion of the coronavirus RNA polymerase gene. Bat no. 14 was trapped in September 2007, while bats 24 and 30 were collected in May 2008; the three bats were from different caves (Table 1). The sequence of the amplified portion of the coronavirus gene most closely resembled those of the RMBCV sequence detected in M. occultus (Dominguez et al., 2007) and E. fuscus in Colorado (Dominguez et al., 2007). A comparison of the sequences (Fig. 2) using CLUSTAL_X showed that the sequences of viruses from M. lucifugus bats 14 and 24 were very similar. All three sequences were closely related to sequences amplified from M. occultus but had several differences from those amplified from E. fuscus (Dominguez et al., 2007).
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When the 500 bp segment from the Myotis coronavirus was compared with corresponding sequences from coronaviruses detected in bats in North America, Europe and South-East Asia (Fig. 3), the sequences of the Myotis coronavirus most closely resembled sequences from Group 1 coronaviruses, including viruses from the other North American bats and Asian bats Rhinolophus sinicus, Myotis ricketti and Miniopterus australis (Woo et al., 2006). In our analysis, the sequences of coronaviruses detected in European bats (Gloza-Rausch et al., 2008) formed a distinct clade within the group 1 coronaviruses.
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Using a strategy that exploited the circular nature of polyomavirus genomes (Johne et al., 2006), we recovered the entire genome of the virus detected in two Myotis species. Analysis of the complete sequence of the viral genomes recovered from three animals revealed an as-yet undescribed polyomavirus. We suggest that the virus should be called Myotis polyomavirus (MyPyV). The genome of MyPyV appeared to have the same arrangement of genes as other polyomaviruses, with potential ORFs for the capsid proteins VP1, VP2 and VP3. ORFs with potential splice sites, the non-structural proteins Small t and Large T antigens were also present. The genome contained other small ORFs, including one for a potential agno protein. However, we could not detect significant similarity between the deduced amino acid sequence of these ORFs and peptides identified for the better-characterized polyomaviruses.
Some mammalian polyomaviruses cause tumours when susceptible rodents are infected experimentally and the newly discovered Merkel polyomavirus is associated with the aggressive Merkel cell skin cancer in humans (Feng et al., 2008). In addition, both the mouse polyomavirus and pneumotropic virus can cause disease when inoculated into newborn mice. However, the mammalian polyomaviruses are not generally associated with acute disease in natural non-immunocompromised hosts. While the naturally occurring mouse virus does retain its ability to cause fatal disease in newborn mice, infection under natural conditions in feral mice does not result in disease (Carroll et al., 2007), possibly because of the simultaneous transmission of virus and maternal immunity to newborn pups. In contrast with the mammalian viruses, at least two of the avian viruses cause acute, frequently fatal inflammatory disease in some species of psittacine birds and geese (Johne & Müller, 2007). The cycle of infection of most polyomaviruses in natural hosts has not been determined. However, the avian polyomavirus appears to have a unique form of reverse vertical transmission in the European pied flycatcher, where blowfly larvae transmit the virus to nestlings, which then infect the parents through the faecal–oral route (Potti et al., 2007).
Like other mammalian polyomaviruses in natural hosts, MyPyV appears not to cause disease in adult M. lucifugus. We detected the virus in apparently healthy bats in a mating swarm. While the number of bats we examined was too low to reach a definitive conclusion, it is interesting that we only detected the virus in females of two Myotis species. Myotis females rear pups in maternity roosts with little input into offspring care by males. It is tempting to speculate that a natural cycle of infection involving ectoparasites, similar to that of the avian polyomavirus in the European pied flycatcher (Potti et al., 2007), might result in the infection of pups in crowded maternity roosts with subsequent infection of the females.
We detected RNA of a group 1 coronavirus in several of the M. lucifugus examined. Our analysis of the virus depends entirely on the nucleotide sequence of a 500 bp segment of the gene for the viral RNA polymerase. The information was sufficient to determine that we had detected a virus very closely related to RMBCV described by Dominguez et al. (2007). The M. lucifugus virus was most closely related (possibly a variant) to virus detected in M. occultus, but it was distinct from RMBCV from E. fuscus.
Since the discovery of SARS-like coronavirus in bats, several studies screening bats for coronaviruses have led to the discovery of many coronaviruses in bats of Asia, Europe and North America. These viruses appear to have a benign relationship with their Chiroptera hosts and display the diversity and constant population growth dynamics that are characteristic of long virus–host associations (Vijaykrishna et al., 2007). This led some to speculate (Vijaykrishna et al., 2007) that bats may be reservoir hosts for all coronaviruses and that rare spillover and adaptation in other species may have led to the development of coronaviruses of humans, domestic animals and other species.
Climatic and socio-economic changes in the coming years may lead to more frequent contact between bats and humans and domestic animals, increasing the chance of spillover of bat viruses and the emergence of new infectious diseases. While we failed to detect virus in bats killed at a wind energy facility, our sample size from this site was small. We suggest that this aspect of our survey should be repeated with larger numbers of bats, as wind plants are a potentially new source of transmission from cryptic, forest bat species which have historically had extremely low rates of contact with domestic animals or humans. Knowledge of viruses that parasitize bats and ecological factors that govern maintenance in bats may help us to reduce the chance of spillover infection or to ameliorate its effects should it occur. For instance, a catalogue of viruses parasitizing bats and molecular information on their gene products would make it easier to detect a virus in the early stages of an epidemic. It would also speed up the identification of reservoir species. Our preliminary study is a small step in that direction.
This project was funded by the Public Health Agency of Canada. The Sustainable Development Innovation Fund of Manitoba Conservation provided funding for survey work at the wind plant. The authors are indebted to Ms Antonia DeBernardo of PHAC for technical assistance. The authors are also indebted to Manitoba Conservation, Dale Brown of the Speleological Society of Manitoba and Joel Jameson, Tracie Parkinson and Amanda Matheson for assistance with collecting bats in the field.References
Baerwald, E. F., D'Amours, G. H., Klug, B. J. & Barclay, R. M. (2008). Barotrauma is a significant cause of bat fatalities at wind turbines. Curr Biol 18, R695–R696.[CrossRef][Medline]
Betts, B. J. (1998). Roosts used by maternity colonies of silver-haired bats in Northeastern Oregon. J Mammal 79, 643–650.[CrossRef]
Bilecki, L. C. (2003). Bat hibernacula in the Karst landscape of central Manitoba: protecting critical wildlife habitat while managing for resource development. Masters thesis, University of Manitoba, Winnipeg.
Calisher, C. H., Childs, J. E., Field, H. E., Holmes, K. V. & Schountz, T. (2006). Bats: important reservoir hosts of emerging viruses. Clin Microbiol Rev 19, 531–545.
Carrington, C. V. F., Foster, J. E., Zhu, H. C., Zhang, J. X., Smith, G. J. D., Thompson, N., Auguste, A. J., Ramkissoon, V., Adesiyun, A. A. & Guan, Y. (2008). Detection and phylogenetic analysis of group 1 coronaviruses in South American bats. Emerg Infect Dis 14, 1890–1893.[CrossRef][Medline]
Carroll, J., Dey, D., Kreisman, L., Velupillai, P., Dahl, J., Telford, S., Bronson, R. & Benjamin, T. (2007). Receptor-binding and oncogenic properties of polyoma viruses isolated from feral mice. PLoS Pathog 3, e179[CrossRef][Medline]
Chu, D. K., Poon, L. L., Chan, K. H., Chen, H., Guan, Y., Yuen, K. Y. & Peiris, J. S. (2006). Coronaviruses in bent-winged bats (Minopterus spp.). J Gen Virol 87, 2461–2466.
Chua, K. B., Crameri, G., Hyatt, A., Yu, M., Tompang, M. R., Rosli, J., McEachern, J., Crameri, S., Kumarasamy, V. & other authors (2007). A previously unknown reovirus of bat origin is associated with an acute respiratory disease in humans. Proc Natl Acad Sci U S A 104, 11424–11429.
Dobson, A. P. (2005). Virology. What links bats to emerging infectious diseases? Science 310, 628–629.
Dominguez, S. R., O'Shea, T. J., Oko, L. M. & Holmes, K. V. (2007). Detection of group 1 coronaviruses in bats in North America. Emerg Infect Dis 13, 1295–1300.[Medline]
Dreier, J., Stormer, M. & Kleesiek, K. (2005). Use of bacteriophage MS2 as an internal control in viral reverse transcription-PCR assays. J Clin Microbiol 43, 4551–4557.
Feng, H., Shuda, M., Chang, Y. & Moore, P. S. (2008). Clonal integration of a polyomavirus in human Merkel cell carcinoma. Science 319, 1096–1100.
Gloza-Rausch, F., Ipsen, A., Seebens, A., Göttsche, M., Panning, M., Felix Drexler, J., Petersen, N., Annan, A., Grywna, K. & other authors (2008). Detection and prevalence patterns of group I coronaviruses in bats, northern Germany. Emerg Infect Dis 14, 626–631.[CrossRef][Medline]
Gurley, E. S., Montgomery, J. M., Hossain, M. J., Bell, M., Azad, A. K., Islam, M. R., Molla, M. A., Carroll, D. S., Ksiazek, T. G. & other authors (2007). Person-to-person transmission of Nipah virus in a Bangladeshi community. Emerg Infect Dis 13, 1031–1037.[Medline]
Hanna, J. N., Carney, I. K., Smith, G. A., Tannenberg, A. E., Deverill, J. E., Botha, J. A., Serafin, I. L., Harrower, B. J., Fitzpatrick, P. F. & Searle, J. W. (2000). Australian bat lyssavirus infection: a second human case, with a long incubation period. Med J Aust 172, 597–599.[Medline]
Johne, R. & Müller, H. (2007). Polyomaviruses of birds: etiologic agents of inflammatory diseases in a tumor virus family. J Virol 81, 11554–11559.
Johne, R., Enderlein, D., Nieper, H. & Müller, H. (2005). Novel polyomavirus detected in the feces of a chimpanzee by nested broad-spectrum PCR. J Virol 79, 3883–3887.
Johne, R., Wittig, W., Fernández-de-Luco, D., Höfle, U. & Müller, H. (2006). Characterization of two novel polyomaviruses of birds by using multiply primed rolling-circle amplification of their genomes. J Virol 80, 3523–3531.
Jones, K. E., Patel, N. G., Levy, M. A., Storeygard, A., Balk, D., Gittleman, J. L. & Daszak, P. (2008). Global trends in emerging infectious diseases. Nature 451, 990–993.[CrossRef][Medline]
Klug, B. J. & Barclay, R. M. R. (2008). The risk of rabies transmission from bat carcasses to mammalian scavengers at wind energy facilities in Alberta. In Abstracts of the 38th Annual North American Symposium for Bat Research, p. 31.
Lau, S. K., Woo, P. C., Li, K. S., Huang, Y., Tsoi, H. W., Wong, B. H., Wong, S. S., Leung, S. Y., Chan, K. H. & Yuen, K. Y. (2005). Severe acute respiratory syndrome coronavirus-like virus in Chinese horseshoe bats. Proc Natl Acad Sci U S A 102, 14040–14045.
Leroy, E. M., Kumulungui, B., Pourrut, X., Rouquet, P., Hassanin, A., Yaba, P., Délicat, A., Paweska, J. T., Gonzalez, J. P. & Swanepoel, R. (2005). Fruit bats as reservoirs of Ebola virus. Nature 438, 575–576.[CrossRef][Medline]
Luby, S. P., Rahman, M., Hossain, M. J., Blum, L. S., Husain, M. M., Gurley, E., Khan, R., Ahmed, B. N., Rahman, S. & other authors (2006). Foodborne transmission of Nipah virus, Bangladesh. Emerg Infect Dis 12, 1888–1894.[Medline]
Nathwani, D., McIntyre, P. G., White, K., Shearer, A. J., Reynolds, N., Walker, D., Orange, G. V. & Fooks, A. R. (2003). Fatal human rabies caused by European bat Lyssavirus type 2a infection in Scotland. Clin Infect Dis 37, 598–601.[CrossRef][Medline]
Poon, L. L., Chu, D. K., Chan, K. H., Wong, O. K., Ellis, T. M., Leung, Y. H., Lau, S. K., Woo, P. C., Suen, K. Y. & other authors (2005). Identification of a novel coronavirus in bats. J Virol 79, 2001–2009.
Potti, J., Blanco, G., Lemus, J. A. & Canal, D. (2007). Infectious offspring: how birds acquire and transmit an avian polyomavirus in the wild. PLoS One 2, e1276[CrossRef][Medline]
Samaratunga, H., Searle, J. W. & Hudson, N. (1998). Non-rabies Lyssavirus human encephalitis from fruit bats: Australian bat Lyssavirus (pteropid Lyssavirus) infection. Neuropathol Appl Neurobiol 24, 331–335.[CrossRef][Medline]
Taylor, L. H., Latham, S. M. & Woolhouse, M. E. (2001). Risk factors for human disease emergence. Philos Trans R Soc Lond B Biol Sci 356, 983–989.
Towner, J. S., Pourrut, X., Albarino, C. G., Nkogue, C. N., Bird, B. H., Grard, G., Ksiazek, T. G., Gonzalez, J. P., Nichol, S. T. & Leroy, E. M. (2007). Marburg virus infection detected in a common African bat. PLoS One 2, e764[CrossRef][Medline]
Vijaykrishna, D., Smith, G. J., Zhang, J. X., Peiris, J. S., Chen, H. & Guan, Y. (2007). Evolutionary insights into the ecology of coronaviruses. J Virol 81, 4012–4020.
Willis, C. K. R. & Brigham, R. M. (2005). Physiological and ecological aspects of roost selection by reproductive female hoary bats (Lasiurus cinereus). J Mammal 86, 85–94.[CrossRef]
Wong, S., Lau, S., Woo, P. & Yuen, K. Y. (2007). Bats as a continuing source of emerging infections in humans. Rev Med Virol 17, 67–91.[CrossRef][Medline]
Woo, P. C., Lau, S. K., Li, K. S., Poon, R. W., Wong, B. H., Tsoi, H. W., Yip, B. C., Huang, Y., Chan, K. H. & Yuen, K. Y. (2006). Molecular diversity of coronaviruses in bats. Virology 351, 180–187.[CrossRef][Medline]
Woolhouse, M. E. & Gowtage-Sequeria, S. (2005). Host range and emerging and re-emerging pathogens. Emerg Infect Dis 11, 1842–1847.[Medline]
Received 29 January 2009; accepted 31 March 2009.