Abstract
Leptospirosis is the most common bacterial zoonosis globally. The pathogen, Leptospira spp., is primarily associated with rodent reservoirs. However, a wide range of other species has been implicated as reservoirs or dead‐end hosts. We conducted a survey for Leptospira spp. in bats and rodents from Papua New Guinea. Kidney samples were collected from 97 pteropodid bats (five species), 37 insectivorous bats from four different families (six species) and 188 rodents (two species). Leptospires were detected in a high proportion of pteropodid bats, including Nyctimene cf. albiventer (35%), Macroglossus minimus (34%) and Rousettus amplexicaudatus (36%). Partial sequencing of the secY gene from rodent and bat leptospires showed host species clustering, with Leptospira interrogans and L. weilii detected in rodents and L. kirschneri and a potential novel species of Leptospira detected in bats. Further research is needed in Papua New Guinea and other locales in the Pacific region to gain a better understanding of the circulation dynamics of leptospires in reservoir species and the risks to public and veterinary health.
Keywords: bats, leptospira, Papua New Guinea, rats, rodents
1. INTRODUCTION
Leptospirosis is a zoonosis of global distribution with the highest incidence rates reported in tropical areas. A systematic review conducted in the Pacific Islands showed that human and animal leptospirosis is widespread in the region while displaying some epidemiological heterogeneity (Guernier et al., 2018). In Papua New Guinea, data are scarce, mostly dating from the 1960s when animal leptospirosis was investigated through microscopy or serology in selected animal species (livestock, dogs, bandicoots and rodents; Guernier et al., 2018). The most recently published survey, conducted in 2004, investigated renal carriage in cattle and pigs from three Papua New Guinea provinces, with the detection of Leptospira borgpetersenii in cattle (Wai'in, 2007). Human cases of leptospirosis in Papua New Guinea have not been investigated for at least 50 years (Emanuel, 1959; Forbes & Wannan, 1955; Kariks & Stallman, 1968; Willis & Wannan, 1966), but the high incidence of this disease in the Pacific region (Guernier et al., 2018), and the prevailing social and environmental conditions in the country (Horwood et al., 2019), make it likely that leptospirosis incidence is very high in this setting. Recent global studies have estimated that the rate of leptospirosis in Papua New Guinea is likely amongst the highest in the world, ranging from > 100 (Costa et al., 2015) to > 500 (Torgerson et al., 2015) cases per 100,000 population.
Bats have been shown to be an important reservoir of leptospires in various tropical islands in the Indian Ocean (Dietrich et al., 2015; Gomard et al., 2016; Lagadec et al., 2012), Malaysia (Thayaparan et al., 2015) and the West Indies (Bevans et al., 2020). However, to date, they have not been investigated in Papua New Guinea, even though the country contains a diverse bat fauna of at least 91 species that includes 21 pteropodids (flying foxes, fruit and blossom bats) and 70 insectivorous bats (Bonaccorsco, 1998; Helgen, 2007).
2. MATERIALS AND METHODS
Bats were trapped using mist nets and harp traps as part of biodiversity surveys conducted in October 2014 in Manus Province (Manus Island) and New Ireland Province (Mussau Island) of Papua New Guinea as previously described (Aplin et al., 2015). Kidney samples were collected from fruit‐eating bats (Pteropodidae): Nyctimene cf. albiventer (n = 29), Macroglossus minimus (n = 35), Rousettus amplexicaudatus (n = 11), Pteropus cf. admiralitatum (n = 17) and Dobsonia anderseni (n = 5); and insectivorous bats: Mosia nigrescens (n = 2) (Emballonuridae), Aselliscus tricuspidatus (n = 5; Hipposideridae), Hipposideros calcaratus and H. cervinus (n = 21; Hipposideridae), Pipistrellus angulatus (n = 1; Vespertilionidae) and Miniopterus cf. propitristis (n = 8; Miniopteridae; Table 1). Animal collections were conducted following approval from the Papua New Guinea Department of Environment and Conservation, the Provincial Governments of Manus and New Ireland. Bat specimens were euthanized with isoflurane inhalation in accordance with an approved animal care and use proposal from the Smithsonian Institution (NHB‐ACUC #2009‐4), exported under permit #014273 (dated 18 November 2014) from the Papua New Guinea Department of Environment and Conservation and deposited and available for study as voucher specimens at the National Museum of Natural History, Smithsonian Institution, Washington. DC, USA.
TABLE 1.
Detection of Leptospira spp. in kidney samples collected from bats and rodents from Papua New Guinea
| Host group (family) | Host genera/species | Collection province a | Leptospira positive (%) |
|---|---|---|---|
| Bats (Pteropodidae) | Nyctimene cf. albiventer | Manus and New Ireland | 10/29 (34.5) |
| Macroglossus minimus | Manus and New Ireland | 12/35 (34.3) | |
| Rousettus amplexicaudatus | Manus and New Ireland | 4/11 (36.4) | |
| Dobsonia anderseni | New Ireland | 0/5 (0) | |
| Pteropus cf. admiralitatum | New Ireland | 0/3 (0) | |
| Bats (Emballonuridae) | Mosia nigrescens | Manus | 0/2 (0) |
| Bats (Hipposideridae) | Aselliscus tricuspidatus | New Ireland | 0/5 (0) |
| Hipposideros cervinus and H. calcaratus | New Ireland | 0/21 (0) | |
| Bats (Vespertilionidae) | Pipistrellus angulatus | Manus | 0/1 (0) |
| Bats (Miniopteridae) | Miniopterus cf. propitristis | New Ireland | 0/8 (0) |
| Rats (Muridae) | Rattus rattus | Eastern Highlands | 8/39 (20.5)b |
| R. exulans | Eastern Highlands | 36/149 (24.2)b |
Rodent specimens (Rattus rattus, n = 39; R. exulans, n = 149) were collected during 2014–2015 as previously described (Robby et al., 2017) in the Eastern Highlands Province of Papua New Guinea. Kidney samples were collected in the field (5–10 mm pieces) and stored in RNAlater (Merck) before transport to the laboratory where they were stored at ‐80°C until testing.
Total nucleic acids were extracted from kidneys using the DNeasy Blood and Tissue kit (Qiagen) according to the manufacturer's instructions. Extracts were screened for pathogenic Leptospira spp. with a TaqMan real‐time polymerase chain reaction (PCR) targeting the rrs (16S) gene (Smythe et al., 2002). Leptospira‐positive samples were subjected to conventional PCR amplification, targeting the secY gene (549‐bp fragment), which has been shown to be suitable for species identification and phylogenetic studies (Ahmed et al., 2006; Guernier et al., 2017; Medeiros et al., 2020; Perez & Goarant, 2010; Victoria et al., 2008). All PCRs were run with negative and positive controls. The resulting PCR products were sent to Macrogen for Sanger sequencing.
Consensus sequences and alignments were generated with Geneious Prime 2019.1.1 (Biomatters Ltd). Phylogenetic trees were constructed using PhyML with Smart Model Selection (Guindon et al., 2010; Lefort et al., 2017) with the following settings: the substitution model selection used Akaike Information Criterion; the tree searching used default settings; the phylogeny was based on the maximum‐likelihood method with 1000 bootstraps. Trees were visualized in FigTree v1.3.1 (http://tree.bio.ecd.ac.uk/).
3. RESULTS
In total, kidney samples were collected from 97 pteropodid bats (five species), 37 insectivorous bats from four different families (six species) and 188 rodents (two species). Real‐time PCR screening of these samples resulted in the detection of Leptospira spp. in a high proportion of fruit‐eating bats (Pteropodidae) from N. cf. albiventer (34.5%), M. minimus (34.3%) and R. amplexicaudatus (36.4%; Table 1). Leptospires were also detected from a high proportion of rodents from R. rattus (20.5%) and R. exulans (24.2%) as previously reported (Robby et al., 2017). Molecular testing did not result in the detection of Leptospira sp. in any of the insectivorous bats or the two other species of pteropodid bats. However, we cannot make any definite conclusions about leptospiral carriage in these species as sample sizes were small (one to eight individuals per species, except for Hipposideros spp. for which we collected 21 individuals).
Leptospira‐positive samples (26 bats, 44 rodents) were targeted for conventional PCR (secY gene), and subsequent Sanger sequencing successfully generated Leptospira data from nine bat samples and 30 rodent samples. Micromammals collected from Papua New Guinea were infected with at least four Leptospira species, one of which was possibly an undescribed species (Figure 1). Three leptospires from R. exulans rodents clustered with L. weilii, while the rest of the rodent samples (six R. rattus and 21 R. exulans) clustered with L. interrogans, with a low diversity observed in this cluster. Seven bat leptospires were clustered with L. kirschneri, with a high diversity observed and host species‐associated clustering. The remaining three bat (all R. amplexicaudatus) leptospires clustered together and were closely related to L. alexanderi and L. mayottensis but did not belong to these species (maximum of 91% similarity when basic local alignment seach tool searched against the National Center for Biotechnology Information database). Interestingly, one R. amplexicaudatus was co‐infected with two different Leptospira (OM811606 and OM811607; Figure 1).
FIGURE 1.

Maximum‐likelihood (ML) phylogenetic tree (model GTR+G+I; 1000 replicates) inferred from the Leptospira secY gene (515‐bp sequence). Phylogenetic trees were constructed using PhyML based on the ML method with 1000 bootstraps. Trees were visualized in FigTree v1.3.1 (http://tree.bio.ecd.ac.uk/). Leptospira secY sequences from Papua New Guinea are shown in blue (GenBank accession numbers OM811598 to OM811638), sequences from other countries are in black. Names include Leptospira species (when provided in GenBank), identifier or GenBank accession number, country of collection and host species. Sequences not from GenBank are from a global collection previously published (Nalam et al., 2010). The four genetic groups including Papua New Guinea samples are highlighted in colour. Bootstrap values higher than 70% are indicated by a dark circle. Black silhouettes represent Papua New Guinea host groups (i.e., rodents or bats). Of note, sample OM811605 (Leptospira from a Rousettus amplexicaudatus) was not included in this phylogeny as the secY sequence was incomplete (476 bp). * Leptospira OM811606 and OM811607 were obtained from the same individual (co‐infection).
To see how Papua New Guinean bat leptospires compared to Leptospira collected from other bats worldwide, we built a phylogeny including 42 secY Leptospira sequences from bats only (Figure 2). The first Leptospira genetic cluster from Papua New Guinean bats was most closely related to a Leptospira kirschneri strain infecting M. natalensis collected in South Africa. The second Leptospira cluster from Papua New Guinean bats was detected in four R. amplexicaudatus individuals and was putatively an undescribed species closely related to L. alexanderi and L. mayottensis. The most closely related sequences to this potential undescribed species were from genetically related Leptospira infecting other Rousettus species collected in South Africa and Madagascar.
FIGURE 2.

ML phylogenetic tree (model HKY85+G+I; 1000 replicates) inferred from the Leptospira secY gene (471‐bp sequence) from bats only. Phylogenetic trees were constructed using PhyML based on the ML method with 1000 bootstraps. Trees were visualized in FigTree v1.3.1 (http://tree.bio.ecd.ac.uk/). Leptospira secY sequences from Papua New Guinea are shown in blue, sequences from other countries are in black. Names include Leptospira species (when provided in GenBank), identifier or GenBank accession number, country of collection and host species. GenBank accession numbers for our study are OM811598 to OM811638.
4. DISCUSSION
Although human leptospirosis has not been recently described in Papua New Guinea, it was confirmed in the 1950s and 1960s (; Emanuel, 1959; Forbes & Wannan, 1955; Kariks & Stallman, 1968; Willis & Wannan, 1966) mostly through seroprevalence studies in the general population. The detection of several species of pathogenic Leptospira in various micromammals in this study, especially L. interrogans in rodents (a Leptospira species commonly related to human clinical cases worldwide) suggests that human leptospirosis is underdiagnosed in Papua New Guinea. The genetic clustering of the rodent leptospires detected in this study with regional human cases further supports the importance of rodents as the primary reservoir for human cases of leptospirosis.
The findings from this study suggest that fruit‐eating bats (Pteropodidae) may be an underappreciated reservoir of Leptospira spp. in Papua New Guinea and potentially other locales in the Pacific region. Previous studies have found a similar prevalence of leptospires in bats from Australia (11%; Cox et al., 2005), Madagascar (35%; Lagadec et al., 2012), China (50%; Han et al., 2018) and Grenada (27%; Bevans et al., 2020). Leptospira kirschneri was the most commonly detected leptospire in Papua New Guinean bats, with the strains clustering in a distinct clade despite the samples being from three different genera of bats and the two collection sites on different island provinces separated by > 400 km. A potential novel Leptospira sp. was also detected in three R. amplexicaudatus bats, adding to previous reports of the detection of diverse Leptospira species in bats (Dietrich et al., 2015). This finding shows the potential circulation of an undescribed Leptospira species in Papua New Guinea but also highlights the rich biodiversity of this phylum yet to be discovered, in bats especially. The Leptospira‐positive samples from 17 bats and 14 rodents that we were unable to sequence could hide further diversity, and uncultured samples might prove insufficient to sequence and uncover undescribed Leptospira species. Comprehensive one‐health studies that consider multiple potential reservoirs and the risk factors for zoonotic transmission are needed to gain a greater understanding of the transmission dynamics between leptospiral reservoirs such as rodents and bats and the potential role that bat‐borne leptospires may play in the public and veterinary health threat of leptospirosis. To date, the role of bats in the transmission of leptospirosis to humans is unclear as direct transmission has not been conclusively established. However, the increasing encroachment of humans into bat habitats coupled with certain cultural practices may increase the risk for zoonotic cross‐over in some settings as established for the transmission of Nipah virus from bats to humans in Bangladesh (McKee et al., 2021).
This study is the first investigation of the molecular diversity of leptospires in Papua New Guinean micromammals and the first to report the detection of leptospires in Papua New Guinean bats. The results show that Papua New Guinean rodents and bats carry diverse Leptospira sp. that are phylogenetically related to strains with known public and veterinary health impacts. Although leptospirosis has not been recently reported in Papua New Guinea, this is likely due to the lack of diagnostic capacity in most hospitals in the country (Greenhill et al., 2012). Further studies are needed to determine the public health burden of leptospirosis in Papua New Guinea and the transmission links with rodents, bats and other animals.
AUTHOR CONTRIBUTIONS
P. F. Horwood and M. Y. Abdad sourced funding for the initial phases of the project and designed the experiments and supervized field and laboratory activities for the study. S Javati, M. Jonduo, S. Robby, J. Kimopa and T. Maure conducted the laboratory testing and molecular analysis of samples. V. Guernier‐Cambert conducted the sequence and phylogenetic analysis of Leptospira spp. K. Aplin and K. M. Helgen conducted identification of bat species. E. S. McBryde and W. Pomat provided high‐level support for the project and sourced funding for sequence analysis of Leptospira spp. P. F. Horwood wrote the first draft of the manuscript with assistance from V. Guernier‐Cambert and M. Y. Abdad. All authors contributed to revisions of manuscript drafts and approved the final document for submission.
CONFLICT OF INTEREST
The authors declare that they have no conflicts of interest.
ETHICS STATEMENT
The authors confirm that the ethical policies of the journal, as noted on the journal's author guidelines page, have been adhered to and the appropriate ethical review committee approval has been received. All relevant guidelines for the use of animals in scientific studies were followed.
Supporting information
SUPPLEMENTARY TABLE 1 Sample information and GenBank accessions numbers for Leptospira sp. sequences generated in this study
ACKNOWLEDGEMENTS
The research team would like to thank the Wildlife Conservation Society (WCS; Nathan Whitmore and Richard Cuthbert) team for organising the fieldwork and allowing the collected samples to be used for the work presented here. Leptospira analysis of the samples was supported by grant funding from the Australian Government through the Department of Foreign Affairs and Trade: Tropical partnerships to strengthen health systems responses to infectious diseases threats (PI: E.S. McBryde). The views expressed in this publication are the authors’ alone and are not necessarily the views of the Australian Government.
Open access publishing facilitated by James Cook University, as part of the Wiley ‐ James Cook University agreement via the Council of Australian University Librarians.
Javati, S. , Guernier‐Cambert, V. , Jonduo, M. , Robby, S. , Kimopa, J. , Maure, T. , McBryde, E. S. , Pomat, W. , Aplin, K. , Helgen, K. M. , Abdad, M. Y. , & Horwood, P. F. (2022). Diversity of Leptospira spp. in bats and rodents from Papua New Guinea. Transboundary and Emerging Diseases, 69, 4048–4054. 10.1111/tbed.14725
Sarah Javati, Vanina Guernier‐Cambert, Mohammad Yazid Abdad and Paul F. Horwood contributed equally to this article.
Present address: Vanina Guernier‐Cambert, Institute of Ecology and Environmental Sciences of Paris (iEES‐Paris), IRD, Sorbonne Université, Paris, France.
Contributor Information
Mohammad Yazid Abdad, Email: yazid@tropmedres.ac.
Paul F. Horwood, Email: paul.horwood@jcu.edu.au.
DATA AVAILABILITY STATEMENT
Information on the samples and sequence information generated are presented in Supplementary Table 1. All Leptospira sp. sequences were deposited in GenBank (accession numbers OM811598 to OM811638).
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
SUPPLEMENTARY TABLE 1 Sample information and GenBank accessions numbers for Leptospira sp. sequences generated in this study
Data Availability Statement
Information on the samples and sequence information generated are presented in Supplementary Table 1. All Leptospira sp. sequences were deposited in GenBank (accession numbers OM811598 to OM811638).
