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PLOS Neglected Tropical Diseases logoLink to PLOS Neglected Tropical Diseases
. 2024 Jul 8;18(7):e0012306. doi: 10.1371/journal.pntd.0012306

Molecular surveillance of zoonotic pathogens from wild rodents in the Republic of Korea

Kyoung-Seong Choi 1,*, Sunwoo Hwang 1, Myung Cheol Kim 2, Hyung-Chul Cho 1, Yu-Jin Park 1, Min-Jeong Ji 1, Sun-Woo Han 3, Joon-Seok Chae 3
Editor: Colleen B Jonsson4
PMCID: PMC11257403  PMID: 38976750

Abstract

Background

Rodents are recognized as major reservoirs of numerous zoonotic pathogens and are involved in the transmission and maintenance of infectious diseases. Furthermore, despite their importance, diseases transmitted by rodents have been neglected. To date, there have been limited epidemiological studies on rodents, and information regarding their involvement in infectious diseases in the Republic of Korea (ROK) is still scarce.

Methodology/Principal findings

We investigated rodent-borne pathogens using nested PCR/RT-PCR from 156 rodents including 151 Apodemus agrarius and 5 Rattus norvegicus from 27 regions in eight provinces across the ROK between March 2019 and November 2020. Spleen, kidney, and blood samples were used to detect Anaplasma phagocytophilum, Bartonella spp., Borrelia burgdorferi sensu lato group, Coxiella burnetii, Leptospira interrogans, and severe fever with thrombocytopenia syndrome virus (SFTSV). Of the 156 rodents, 73 (46.8%) were infected with Bartonella spp., 25 (16.0%) with C. burnetii, 24 (15.4%) with L. interrogans, 21 (13.5%) with A. phagocytophilum, 9 (5.8%) with SFTSV, and 5 (3.2%) with Borrelia afzelii. Co-infections with two and three pathogens were detected in 33 (21.1%) and 11 rodents (7.1%), respectively. A. phagocytophilum was detected in all regions, showing a widespread occurrence in the ROK. The infection rates of Bartonella spp. were 83.3% for B. grahamii and 16.7% for B. taylorii.

Conclusions/Significance

To the best of our knowledge, this is the first report of C. burnetii and SFTSV infections in rodents in the ROK. This study also provides the first description of various rodent-borne pathogens through an extensive epidemiological survey in the ROK. These results suggest that rodents harbor various pathogens that pose a potential threat to public health in the ROK. Our findings provide useful information on the occurrence and distribution of zoonotic pathogens disseminated among rodents and emphasize the urgent need for rapid diagnosis, prevention, and control strategies for these zoonotic diseases.

Author summary

Rodents live almost everywhere in the world, adapt to extremely diverse habitats, and transmit various infectious diseases to humans and other animals. All six pathogens were detected in rodents. Our findings demonstrated that 66.7% (104/156) of rodents were infected with at least one pathogen. We also observed differences in the pathogens detected in rodents by province. These results provide evidence that rodents play an important role in the transmission of SFTSV. Although we did not screen for all rodent-borne diseases, these data provide information about emerging rodent-borne diseases disseminated in the ROK and emphasize the risk of occurrence of rodent-borne diseases.

Introduction

Rodents are globally abundant and well-known reservoirs and vectors of infectious diseases that affect both livestock and humans [1, 2]. The current global change context (e.g., land-use change, urbanization, and temperature increase) is particularly suitable for the expansion of several rodent species beyond their natural distribution areas [3,4]. Rodents are widespread in rural and urban areas and cause numerous human infections in regions where humans are in close contact with them. Rodents are reservoir hosts for at least 60 zoonotic diseases and play a vital role in disease transmission by spreading disease directly through contact or bites or indirectly through arthropods or food contamination [57]. Despite their potential threat to public health, there has not been much focus on diseases transmitted by rodents [8,9]. Moreover, the control of rodents is difficult due to their behavioral plasticity, life history traits, and high breeding potential [3].

Anaplasma phagocytophilum is a tick-transmitted, obligatory intracellular zoonotic bacterium that infects the neutrophils of various hosts, including humans, dogs, cats, horses, domestic, and wild animals [1013]. The clinical signs of A. phagocytophilum infection range from asymptomatic to serious symptoms of veterinary and public health importance. The occurrence of A. phagocytophilum infection is increasing along with climate change worldwide. A broad variety of animal species are known to harbor A. phagocytophilum, and humans are incidental dead-end hosts [14]. Vertebrate hosts are crucial for the maintenance and circulation of this pathogen in enzootic foci. In particular, small rodents and wild ruminants have been suggested as primary reservoirs [1519]. In the United States, the white-footed mouse (Peromyscus leucopus) is considered a well-established reservoir species [20,21]. In the Republic of Korea (ROK), A. phagocytophilum has also been detected in small mammals such as rodents and shrews (Crocidura lasiura) [22,23].

Bartonella spp. are facultative intracellular bacteria that cause persistent infections in the erythrocytes and endothelial cells of mammalian hosts [24]. The clinical manifestations caused by these species are characterized by fever, endocarditis, myocarditis, neuroretinitis, lymphadenopathy, and a range of vascular pathologies [2428]. More than 30 Bartonella spp. and three subspecies are currently recognized [29], and at least 20 species are associated with rodents, indicating that rodents serve as potential reservoirs for zoonotic Bartonella spp. [3032]. Among the rodent-adapted Bartonella spp., B. elizabethae, B. grahamii, B. rochalimae, B. tribocorum, B. vinsonii, and B. washoensis have been found to cause human infections [32,33]. In general, Bartonella spp. have been considered to be transmitted by arthropods [24,31]. Although Bartonella infections are widely distributed in rodents in different geographic regions [3441], there is very little information on the distribution and prevalence of these species in rodents in the ROK [22,42,43].

Lyme borreliosis (LB) is one of the most common vector-borne diseases in North America and Eurasia and is caused by a spirochete belonging to the Borrelia burgdorferi sensu lato (s.l.) group [44]. Among this group, B. burgdorferi sensu stricto (s.s.), B. afzelii, and B. garinii are the major causative agents of LB in humans and exhibit different geographical distributions [45,46]. These species are transmitted between vertebrate hosts and tick vectors [47]. B. burgdorferi s.s. occurs in North America and Europe and has various reservoir hosts (e.g., rodents and birds), whereas B. afzelii and B. garinii occur in Eurasia and can only use specific vertebrate hosts, namely, rodents and birds, respectively [44,45]. Different Borrelia species cause different symptoms in humans. For instance, B. burgdorferi s.s. infection is associated with Lyme arthritis, whereas B. garinii is mostly linked to neuroborreliosis, and B. afzelii infection is related to a chronic skin condition known as acrodermatitis [44,4850]. In the ROK, B. burgdorferi s.l. was first detected in 1993 and has been sporadically identified in ticks, dogs, horses, wild rodents, and humans [5156].

Coxiella burnetii is an obligate intracellular bacterium with a worldwide distribution and is the causative agent of Q fever in humans and a wide range of animals [57]. It is highly infectious and has the ability to form spore-like particles that can withstand harsh environmental conditions and can be easily dispersed by airflow [58]. Humans acquire C. burnetii infection through inhalation of contaminated aerosols or dust particles [59]. Q fever is a public health concern as it ranks as one of the 13 leading global priority zoonoses. Moreover, it has been considered a potential biological weapon due to its widespread availability, aerosolized spread, and environmental stability [60]. The clinical manifestations of C. burnetii infection include fever and flu-like symptoms. The major sources of these infections are infected ruminants, which experience issues of abortion and infertility. Ticks and rodents are also known as natural reservoirs of C. burnetii [61]. Other studies have recently performed molecular characterization of this pathogen in domestic animals in the ROK [57,62]; however, these studies had a limited spatial distribution and were species-specific.

Leptospirosis is a zoonotic infectious disease with a global distribution and is caused by a spirochete of the genus Leptospira [63,64]. It infects more than one million people annually, with 60,000 deaths recorded [65]. Leptospira is maintained in several wild and domestic animal hosts through renal carriage and is excreted in the urine for several months [66,67]. Infection in humans and animals primarily occurs through direct contact with the urine of infected hosts or indirect exposure to contaminated water, soil, or food [68]. Its clinical manifestations in humans range from a mild febrile illness to life-threatening renal failure, pulmonary hemorrhage, and/or cardiac complications [69]. Recent studies have suggested that an increase in the incidence of leptospirosis in humans is often associated with heavy rainfall and flooding [70,71]. Rodents are considered the most important reservoir of pathogenic Leptospira spp. and contribute to disease transmission because of their close contact with humans and domestic animals [72]. L. interrogans, L. borgpetersenii, and L. kirschneri are the most abundant species circulating in humans and animals worldwide [73], with L. interrogans being the most commonly described in rodents [72].

Severe fever with thrombocytopenia syndrome (SFTS) is an emerging tick-borne viral disease that has been primarily reported in China, the ROK, Japan, Vietnam, and Taiwan [7478]. SFTS is formally caused by Bandavirus dabieense [also commonly known as SFTS virus (SFTSV)], which belongs to the genus Bandavirus in the family Phenuiviridae. SFTSV infections are characterized by high fever, fatigue, myalgia, gastrointestinal symptoms, thrombocytopenia, and multiorgan failure [74,79]. SFTSV can also spread from person to person through exposure to the blood of an infected individual [80]. Due to its potential as a public health threat, SFTS was chosen as one of nine emerging diseases given a priority for research by the World Health Organization in 2017 [81]. As humans are often in close contact with domestic animals and may encounter rodents when they work outdoors, transmission between animals and humans is another possible major transmission route [82]. The overall mortality rate of this disease has been reported to be 3–30% in different countries [74,83,84]. Although SFTSV has been identified in various animals, its natural reservoir hosts have not been determined.

As demonstrated in the abovementioned studies, rodents may be involved in the transmission cycles of various diseases. Recently, the incidences of several infectious diseases have been rapidly increasing worldwide due to climate warming. Rodent populations are also growing exponentially due to climate change and urbanization. To date, most studies on rodent-borne diseases in the ROK have been primarily focused on identifying hantavirus infections. Although rodents are considered important reservoirs of zoonotic infectious pathogens, epidemiological information regarding their involvement in infectious diseases is limited in the ROK. Therefore, the aims of this study were to investigate the occurrence of some rodent-borne diseases, characterize their genetic relationships, and determine the roles of rodents as reservoir hosts for these diseases.

Methods

Ethical statement

Rodent collection was approved by the Seoul National University Institutional Animal Care and Use Committee (No. SNU-190524-2-1) and performed according to the Seoul National University Guidelines on the care and use of laboratory animals.

Sample collection

Rodents were captured using Sherman traps (3 × 3.5 × 9-inch folding traps; H.B. Sherman Traps, Tallahassee, FL, USA) from 27 regions in eight provinces across the country between March 2019 and November 2020. Rodents were captured from at least one region in each province (S1 Table). The traps were set in locations where human infections with SFTSV had been reported based on statistical data from the Korea Disease Control and Prevention Agency. To capture rodents, rural (agricultural land such as regions with rivers, valleys, mountains, and lakes) and peri-urban (human residential and farm) areas were selected. Rural areas were defined as regions with natural landscapes and minimal urban impact, whereas peri-urban areas were defined as transitional zones between urban and rural areas. A total of 60 traps were installed in each capture region in lines in 3-m intervals between 5 p.m. and 6 p.m. and retrieved the next day between 9 a.m. and 10 a.m. after setup: 60 traps per night were set in each region. The capture duration for every site was 14–15 h, and each capture site was sampled only once. The captured rodents [rural (n = 127) and peri-urban (n = 29)] were transported to the laboratory in an icebox with the traps, morphologically identified, and euthanized using CO2. Thereafter, blood, spleen, and kidney samples were collected from each animal. A whole blood sample was also collected in a serum separation tube, and the serum was separated and used for RNA extraction.

DNA/RNA extraction and PCR analysis

DNA was extracted from spleen (10 mg) and kidney (25 mg) samples using the DNeasy Blood & Tissue Kit (Qiagen, Hilden, Germany) according to the manufacturer’s instructions and stored at −20°C until analysis. Splenic DNA was subjected to PCR amplification to detect A. phagocytophilum, Bartonella spp., Borrelia spp., and C. burnetii, and kidney DNA was subjected to PCR to detect L. interrogans. These pathogens were screened using each specific primer with the nested PCR method under the following conditions: 93–95°C for 5 min, followed by 30–40 cycles of 93–95°C for 1 min, the annealing temperature of each pathogen, 72°C for 1 min, and a final extension step at 72°C for 10 min (Table 1). Distilled water was used as a negative control in all PCR analyses. Secondary PCR products were visualized on 1.5% agarose gels stained with ethidium bromide.

Table 1. Primer information used for PCR analysis.

Pathogen Target genes Sequences (5′–3′) Sizes
(bp)
Annealing temp./Time
Anaplasma phagocytophilum 16S rRNA TCCTGGCTCAGAACGAACGCTGGCGGC 1,433 50°C/30 s
AGTCACTGACCCAACCTTAAATGGCTG
GTCGAACGGATTATTTTTATAGCTTGC 926 56°C/30 s
CCCTTCCGTTAAGAAGGATCTAATCTCC
Bartonella spp. ITS TTCAGATGATGATCCCAAGC 639 55°C/30 s
AACATGTCTGAATATATCTTC
CCGGAGGGCTTGTAGCTCAG 499 55°C/30 s
CACAATTTCAATAGAAC
Borrelia spp. ospA GGGAATAGGTCTAATATTAGCC 665 42°C/60 s
CACTAATTGTTAAAGTGGAAGT
GCAAAATGTTAGCAGCCTTGAT 392 56°C/60 s
CTGTGTATTCAAGTCTGGC
Coxiella burnetii IS1111 TATGTATCCACCGTAGCCAGTC 687 54°C/30 s
CCCAACAACAACCTCCTTATTC
GAGCGAACCATTGGTATCG 203 54°C/30 s
CTTTAACAGCGCTTGAACGT
Leptospira interrogans rpoB GTTCCAACATGCAACGYCAR 1,649 52°C/60 s
GTTGAAGGATTCRGGRATAC
TYATGCCKTGGGAAGGWTAC 1,023 56°C/30 s
GCATRTCRTCKGACTTGATG
SFTSV S CATCATTGTCTTTGCCCTGA 461 52°C/40 s
AGAAGACAGAGTTCACAGCA
AAYAAGATCGTCAAGGCATCA 346 55°C/40 s
TAGTCTTGGTGAAGGCATCTT

*SFTSV: severe fever with thrombocytopenia syndrome virus

RNA was extracted from 200-μL aliquots of serum using the Gene-spin Viral DNA/RNA Extraction Kit (iNtRON Biotechnology, Seongnam, ROK) according to the manufacturer’s instructions. The viral RNA was stored at − 80°C until use. Each RNA sample was tested using nested reverse transcription-polymerase chain reaction (RT-PCR) assays to detect the small (S) segment of SFTSV. Primary PCR was performed using one-step RT-PCR premix (Solgent, Daejeon, ROK) under the following conditions: initial step of 30 min at 50°C and 15 min at 95°C for denaturation, followed by 40 cycles of 20 s at 95°C, 40 s at 52°C, and 30 s at 72°C, with a final extension step of 5 min at 72°C. Nested PCR was conducted using 1 μL of the primary PCR product as a template (BIOFACT, Daejeon, ROK). The reaction for the nested PCR consisted of 25 cycles of 20 s at 94°C, 40 s at 55°C, and 30 s at 72°C. The primer information used to detect SFTSV is listed in Table 1. Secondary PCR products were visualized on 1.5% agarose gels stained with ethidium bromide.

Phylogenetic analysis

The secondary PCR products were purified using the AccuPrep PCR Purification Kit (Bioneer, Daejeon, ROK) according to the manufacturer’s instructions and directly sequenced (Macrogen Inc., Seoul, ROK). Less than five PCR-positive samples from each pathogen were utilized for all sequencing analyses. In cases in which there were more than five positive samples, we selected only a few samples and used them for the sequencing analysis. All the nucleotide sequences obtained for each pathogen were aligned using the BioEdit software and then compared with reference sequences from the National Center for Biotechnology Information database (http://www.ncbi.nlm.nih.gov) to determine their similarity using Geneious Prime 2022.2 software (http://www.geneious.com). Phylogenetic analysis of each pathogen was performed using the maximum-likelihood method implemented in MEGA11 using the best substitution model. Bootstrap values were calculated by analyzing 1,000 replicates to evaluate the reliability of clusters. The models used in this study were K2 + G for A. phagocytophilum, Tamura 3-parameter + G + I for Bartonella spp., Tamura-Nei for Borrelia spp., and the Kimura 2-parameter model for C. burnetii, L. interrogans, and SFTSV. The nucleotide sequences obtained in this study were assigned the following accession numbers: OR287077-OR287091 for A. phagocytophilum, OR288176-OR288190 for B. grahamii, OR288191-OR288193 for B. taylorii, OR284310-OR284311 for B. afzelii, OR284312-OR284321 for C. burnetii, OR284322-OR284324 for L. interrogans, and OR257718-OR257726 for SFTSV.

Statistical analysis

The infection rates were calculated with 95% confidence intervals (CIs). The PCR results for each rodent sample were recorded as negative or positive and were categorized as a single infection or a co-infection with two or three pathogens. Statistical analysis was performed using the SPSS 29.0 software package for Windows (SPSS Inc., Chicago, IL, USA). The association between sex and the infection rate for each pathogen was determined using the chi-square test. A P-value ≤ 0.05 was considered statistically significant.

Results

Sample collection

A total of 175 rodents were captured and morphologically classified as follows: 151 Apodemus agrarius (striped field mouse) (70 males and 81 females), 5 Rattus norvegicus (Norway rat) (2 males and 3 females), and 19 unknown. A. agrarius was found in most of the capture sites in the ROK, whereas R. norvegicus was captured only in two provinces (Table 2). Unknown samples were excluded from this study, and the remaining 156 rodents were used for data analysis.

Table 2. Number of rodents captured by province.

Province Apodemus agrarius Rattus norvegicus Total
Gyeonggi 12 - 12
Gangwon 18 - 18
Chungbuk 19 - 19
Chungnam/Daejeon 4 - 4
Jeonbuk 13 - 13
Jeonnam 4 - 4
Gyeongbuk 76 4 80
Gyeongnam 5 1 6
Total 151 5 156

“-”: no rodents captured

Prevalence of pathogens detected in the captured rodents

The presence of six pathogens was investigated by PCR analysis from the two species, A. agrarius and R. norvegicus. Of the 156 rodents, 104 (66.7%; 95% CI: 59.3–74.1) were infected with at least one pathogen. The infection rate was 64.3% in females (54/84) and 66.6% in males (48/72). There was no significant difference between single infection or co-infections and sex (P = 0.886). The infection rates of each pathogen by sex are shown in Table 3. In all the six pathogens, no significant difference was found in the infection rate between the sexes (Table 3).

Table 3. Association between each pathogen and the sex of the captured rodents.

Pathogens Male (n = 72) Female (n = 84) χ2 (P-value)
A. phagocytophilum 9 12 0.008 (0.928)
Bartonella spp. 40 33 3.494 (0.062)
Borrelia spp. 2 3 0.000 (1.000)
C. burnetii 9 16 0.796 (0.372)
L. interrogans 12 12 0.035 (0.851)
SFTSV 4 5 0.000 (1.000)
Total 48 54 0.020 (0.886)

*P < 0.05

**P < 0.005

In terms of pathogens, Bartonella spp. were frequently detected (46.8%; 95% CI: 39.0–54.6), followed by C. burnetii (16.0%; 95% CI: 10.2–21.8), L. interrogans (15.4%; 95% CI: 9.7–21.1), A. phagocytophilum (13.5%; 95% CI: 8.1–18.9), SFTSV (5.8%; 95% CI: 2.1–9.5), and Borrelia spp. (3.2%; 95% CI: 0.4–6.0) (Table 4). The details of the pathogens identified by province are shown in Table 4. All six pathogens were detected in Gangwon, Chungbuk, and Gyeongbuk provinces. Five of the six pathogens, excluding SFTSV, were found in Gyeongnam province, whereas only one pathogen was detected in Chungnam and Jeonnam provinces (Table 4). Co-infections with two and three pathogens from the captured rodents were also detected in 33 (21.2%; 95% CI: 14.8–27.6) and 11 (7.1%; 95% CI: 3.1–11.1) animals, respectively (Table 5), and co-infections with Bartonella spp. and L. interrogans were the most frequently detected (Table 5). Information regarding the pathogens identified by region is shown in the map in (Fig 1).

Table 4. Number of positive samples in which pathogens were identified in captured rodents according to each province.

Province A. phagocytophilum Bartonella spp. Borrelia spp. C. burnetii L. interrogans SFTSV
Gyeonggi (n = 12) 1 5 - - 2 2
Gangwon (n = 18 4 12 1 5 6 1
Chungbuk (n = 19) 3 10 1 2 6 2
Chungnam/Daejeon (n = 4) 1 - - - - -
Jeonbuk (n = 13) 3 8 - 3 - -
Jeonnam (n = 4) 1 - - - - -
Gyeongbuk (n = 76) 7 32 2 14 6 4
Gyeongnam (n = 5) 1 6 1 1 4 -
Total (n = 151) 21 (13.5%) 73 (46.8%) 5 (3.2%) 25 (16.0%) 24 (15.4%) 9 (5.8%)

“-”: not detected.

Table 5. Co-infections of two or three pathogens detected in captured rodents.

Pathogens No. of positive samples
A. phagocytophilum + Bartonella spp. 7
A. phagocytophilum + Borrelia spp. 1
A. phagocytophilum + C. burnetii 1
Bartonella spp. + Borrelia spp. 2
Bartonella spp. + C. burnetii 7
Bartonella spp. + L. interrogans 10
Bartonella spp. + SFTSV 3
C. burnetii + L. interrogans 2
A. phagocytophilum + Bartonella spp.+ C. burnetii 1
A. phagocytophilum + Bartonella spp.+ L. interrogans 3
A. phagocytophilum + Bartonella spp.+ SFTSV 2
A. phagocytophilum + C. burnetii + L. interrogans 1
Bartonella spp. + Borrelia spp. + C. burnetii 1
Bartonella spp. + C. burnetii + L. interrogans 1
Bartonella spp. + L. interrogans + SFTSV 2

Fig 1. Maps showing the regions where rodent-borne pathogens were detected in the Republic of Korea.

Fig 1

The word symbol is indicated differently according to each pathogen. Maps were created using NGII [https://www.data.go.kr/data/15062309/fileData.do] and are Korea Open Government License Type 1, which can be freely used without any permission.

Phylogenetic trees of rodent-associated pathogens

Anaplasma phagocytophilum

A. phagocytophilum was detected in rodents from all the examined provinces, indicating that this pathogen is spread throughout the ROK. Of 21 positive samples, 15 were sequenced and confirmed to be A. phagocytophilum by a phylogenetic tree analysis based on the 16S rRNA gene (Fig 2). Our sequences exhibited 97.6–99.9% identity with each other and 95.6–100% identity with those reported in the ROK. These 15 sequences were similar to those previously reported from several different hosts such as cattle, dogs, horses, humans, ticks, and rodents in other countries, sharing 96.9–100% nucleotide identities with these. Furthermore, several variants co-existed in the same geographical area. According to the phylogenetic tree, A. phagocytophilum was divided into clades 1 and 2, and all our sequences from A. agrarius belonged to clade 1 (Fig 2). The difference in sequences between clades 1 and 2 revealed 94.7–98.5% nucleotide identities. Clade 2 had 10 nucleotide differences compared with clade 1. Genetic variants were detected in A. phagocytophilum circulating in the ROK.

Fig 2. Phylogenetic tree inferred by maximum-likelihood analysis using the K2 + G model of the 16S rRNA gene sequence of Anaplasma phagocytophilum.

Fig 2

The numbers at the nodes are bootstrap values expressed as a percentage of 1,000 replicates. The scale bar indicates nucleotide substitution per site. Samples sequenced from Apodemus agrarius are shown in filled circles.

Bartonella spp.

Bartonella spp. were frequently detected in A. agrarius in the ROK, but they were not found in all provinces (Table 4). Bartonella spp. were detected in both A. agrarius and R. norvegicus. Of 73 internal transcribed spacer (ITS) PCR-positive samples, 18 sequences were included in a phylogenetic analysis. Two species of Bartonella spp. were identified circulating in the examined rodents using the phylogenetic tree based on the ITS gene: B. grahamii and B. taylorii (Fig 3). The prevalence of B. grahamii and B. taylorii was 83.3% (15/18) and 16.7% (3/18), respectively. The 15 sequences belonging to B. grahamii showed 94.9–100% identity with each other and formed the same group as B. grahamii found in leeches (KX270012) and A. agrarius (JN810851) reported in the ROK, exhibiting 95.9–99.8% identity with those sequences. Furthermore, another sequence (JN810855) reported from A. agrarius in the ROK demonstrated 87.1–90.8% similarity to the sequences reported in our study. The three sequences classified as B. taylorii exhibited 100% identity with each other and shared 92.5–100% identity with those belonging to this species.

Fig 3. Phylogenetic analysis based on the ITS region of Bartonella spp. (maximum-likelihood analysis using the Tamura 3-parameter + G + I model with 1,000 replicates).

Fig 3

The scale bar indicates nucleotide substitution per site. Sequences determined from A. agrarius are indicated in filled circles.

Borrelia spp.

Borrelia spp. were found in four provinces (Table 4), and the infection rate of Borrelia spp. was the lowest (3.2%) compared with those of the other pathogens identified. Among the five PCR-positive samples, only two sequences were obtained and demonstrated 98.6% identity with each other. A phylogenetic analysis based on the outer surface protein A (ospA) gene revealed that our sequences were assigned to B. afzelii (Fig 4). The two sequences exhibited 98.9–100% homology with those identified previously in A. agrarius in the ROK. Our sequences showed 97.8–100% identity with those belonging to this group. Furthermore, these sequences displayed 98.2–99.6% similarity to those reported in humans from Austria, Germany, the Czech Republic, the ROK, and Sweden.

Fig 4. Maximum-likelihood phylogenetic tree using the Tamura-Nei model based on the ospA gene of Borrelia spp. Bootstrap values were calculated with 1,000 replicates of the alignment.

Fig 4

The scale bar indicates nucleotide substitution per site. Sequences obtained from A. agrarius are symbolized in filled circles.

Coxiella burnetii

C. burnetii was the second most frequently detected pathogen and was identified in both A. agrarius and R. norvegicus. However, it was found in five different provinces. Of 25 positive samples, 10 sequences were included in a phylogenetic tree based on the IS1111 gene. These sequences showed 97.5–100% identity with each other. Only one sequence (OR284314) had the closest genetic relationship with strains identified in febrile and pneumonic patients (KP645188 and JF970260), which are known as virulent strains, exhibiting 100% homology with those (Fig 5). The others formed a separate branch, exhibiting 99.0–99.5% identity with two human isolates (KP645188 and JF970260). The phylogenetic tree revealed the presence of genetic variations within the C. burnetii sequences.

Fig 5. Maximum-likelihood phylogenetic tree from the IS1111 gene of Coxiella burnetii.

Fig 5

The evolutionary analysis was inferred using the Kimura 2-parameter model. Bootstrap values (1,000 replicates) are indicated in each node. The scale bar indicates nucleotide substitution per site. Sequences determined from A. agrarius are highlighted in filled circles.

Leptospira interrogans

L. interrogans was the third most commonly detected pathogen and was also found in both A. agrarius and R. norvegicus. Of 24 positive samples, only three sequences were obtained, and they had 97.7–99.5% identity with each other. A phylogenetic tree based on the RNA polymerase subunit beta (rpoB) gene revealed that these sequences belonged to L. interrogans (Fig 6). Two sequences (OR284322 and OR284323) were classified into L. interrogans serovar Lai and showed 99.2–100% identity with those reported in China and 99.4–100% identity with those reported in A. agrarius in the ROK. The other sequence (OR284324) belonged to L. interrogans serovar Manilae, which has detected in Mus musculus in Japan, exhibiting 98.2% similarity (Fig 6). At least two serovars of L. interrogans were found to be circulating in A. agrarius in the ROK.

Fig 6. Phylogenetic analysis based on the rpoB gene of Leptospira interrogans.

Fig 6

The tree was inferred in MEGA X using maximum-likelihood and Kimura 2-parameter with 1,000 replicates. The scale bar implies nucleotide substitution per site. The box of dash lines indicates L. interrogans. Sequences obtained from A. agrarius are shown in filled circles.

Severe fever with thrombocytopenia syndrome virus

SFTSV was detected in nine A. agrarius samples (5.8%) and found in four different provinces (Table 4). Of the nine SFTSV infections, a single infection with SFTSV was detected only in two A. agrarius samples, and the remaining samples were primarily co-infected with other pathogens such as Bartonella spp. and L. interrogans (Table 5). Nine sequences were obtained and included in the phylogenetic tree. These sequences demonstrated 95.95–100.0% identity with each other. The phylogenetic analysis based on the S segments revealed that five and four sequences were classified into subgenotype B-2 and genotype D, respectively (Fig 7). The sequences belonging to genotype B-2 exhibited 94.5–97.4% homology with those identified in human and other animal samples in the ROK, whereas four sequences showed 99.7–100.0% identity with those identified in human samples. These results revealed that genotype B-2 is prevalent in the ROK and that genetic variants exist within genotype B-2.

Fig 7. Phylogenetic tree of the severe fever with thrombocytopenia syndrome virus based on the analysis of partial sequences of small segments.

Fig 7

Maximum-likelihood analysis was used to construct the Kimura 2-parameter model (1,000 bootstrap replicates). The scale bar implies nucleotide substitution per site. Sequences identified from A. agrarius are indicated in filled circles.

Discussion

This study demonstrated the infection rate and genetic characterization of zoonotic pathogens by molecular analysis in rodents captured from throughout the ROK. Rodents were trapped from rural and peri-urban areas with frequent movement of people, which may be associated with a high probability of disease transmission because humans and rodents share the same space. In the present study, all six pathogens were detected in rodents. The results demonstrated that 66.7% (104/151) of rodents were infected with at least one pathogen. According to our findings, Bartonella spp. were most frequently detected, and Borrelia spp. were the least commonly detected in rodents. Moreover, by sex, there was no difference in the infection rate and no statistically significant differences between single infection and co-infections. A limitation of this study is that the number of captured rodents in each province varied. Nevertheless, five pathogens were identified in Gyeongnam province, which had the second lowest number of rodents captured. In contrast, although more rodents were captured in Gyeonggi and Jeonbuk provinces than in Gyeongnam province, fewer pathogens were detected. These results imply that increased sample numbers do not necessarily correlate with the probability of pathogen detection. Moreover, because most rodents were captured in rural areas, it is impossible to compare the infection rates between rural and peri-urban areas. At this time, we cannot conclude differences in pathogen detection, but this finding may be influenced by the sampling site where the rodents were captured. Although the infection rate was not very high, A. phagocytophilum was found in all provinces. Considering that the number of rodents captured varied by province and that few rodents were captured in some provinces, A. phagocytophilum may be the most widespread pathogen in the ROK. Furthermore, to the best of our knowledge, this is the first study to report C. burnetii and SFTSV infections in rodents in the ROK and to conduct an extensive study to investigate infections with several pathogens. These data provide valuable information for evaluating the potential risk of rodents in public health.

In this study, all six of the evaluated pathogens were detected using the nested PCR method. In general, nested PCR is more sensitive than qPCR but is also prone to contamination and is more cumbersome [85]. There were the discrepancies between PCRs and sequencing results. We cannot address the reason why the sequencing results were not good at this time. This may be the need for more amounts of genetic material to enable proper sequencing. Nonetheless, we considered PCR-positives to be truly positive, regardless of whether the amplicons could be sequenced. It seems difficult to consider them negative only because some amplicons could not be sequenced.

Anaplasma phagocytophilum is known as the third most common tick-borne pathogen in the USA and Europe [86] and has been detected in 20 different rodent species [87]. A. phagocytophilum infection rates range considerably in rodent species [87]; this may be explained by differences in small mammals that maintain tick species. In this study, the prevalence of A. phagocytophilum infections in A. agrarius was 13.5%, which was rather lower than reported in a previous study conducted in the ROK (19.1%) [88]. To date, there has been no report of A. phagocytophilum infection in Rattus spp. in the ROK; however, a high infection rate (31.5%) of A. phagocytophilum has been reported in Rattus spp. from China [89]. A. phagocytophilum has been detected in a variety of animals, including ticks in the ROK, but its pathogenicity still remains unclear. The sequences obtained from rodents showed 97.9–100% identity to A. agrarius (KR611719) reported in the ROK. According to the phylogenetic analysis, there are several genetic variants among A. phagocytophilum circulating in the ROK. Haemaphysalis longicornis, which is found primarily in the ROK, tends to use A. agrarius as the major host to maintain A. phagocytophilum [23,89], indicating that A. agrarius is an enzootic reservoir. Thus, further studies are required to determine the pathogenicity of A. phagocytophilum variants circulating in the ROK.

The overall prevalence of Bartonella spp. in rodents was 46.8%, which was the highest of the prevalence rates of all the other pathogens examined in this study. However, the detection rate in the present study was lower than that described in a previous report (62.0%) based on the ITS gene [43]; this difference may be because of the location where the rodents were captured. Moreover, the prevalence of Bartonella spp. in rodents varies across countries, e.g., 5.5% in Turkey [37], 23.7% in Lithuania [90], 36.3% in Chile [32], 40.4% in Slovenia [34], and 65.8% in Eastern Germany [41]. In addition, the Bartonella spp. that are prevalent in each country are different [27,32,34,38,9093]. According to the phylogenetic tree, B. grahamii has two distinct groups, and the sequences obtained in this study formed the same group and diverged from some sequences previously identified in the ROK. This indicates that genetic variations of B. grahamii exist in the ROK. R. norvegicus and R. rattus are known as major reservoirs for Bartonella spp. in several countries [27,9496], but Bartonella spp. have not been detected in other rodent species or in R. norvegicus in the ROK [22]. The analysis of R. norvegicus in this study was unfortunately limited because only five animals were captured, and their data were excluded. Further studies are necessary to investigate Bartonella spp. infection in R. norvegicus. The present results demonstrated that B. grahamii was the most predominant species, and B. taylorii was found in three rodents, which is consistent with the findings of a previous study [43]. B. grahamii is a zoonotic pathogen that is associated with neuroretinitis and retinal artery occlusion in humans [25]. B. taylorii can cause infection in animals [90], but its pathogenicity remains unclear. In Europe, B. taylorii is the predominant species found in rodents [24,37]. In this study, the Bartonella spp. detected were different by province, and in Jeonbuk province, both B. grahamii and B. taylorii were identified, indicating that the pathogens present in each province are different. Although B. taylorii has been detected in some A. agrarius in the ROK, its transmission route remains unknown. Considering its high infection rate in A. agrarius, potential vectors of this pathogen should be identified to prevent infection.

The detection rate of Borrelia spp. in A. agrarius was 3.2% and was the lowest infection rate compared with those of the other pathogens examined in this study. Our result was different from those of previous studies that evaluated heart samples from A. agrarius (29.6%) [56] and ticks (33.6%) collected from wild rodents in the ROK [97]. This finding can be explained by the differences in the genes and samples used. For instance, Kim et al [56] reported that B. burgdorferi s.s. and B. garinii infected the spleen and that B. afzelii exhibited a high detection rate in the heart; however, B. burgdorferi s.s. and B. garinii were not detected in the spleen. It is speculated that the number of positive samples was small and could not be detected. Among the Borrelia burgdorferi s.l. group, only B. afzelii was identified in A. agrarius, which supports previous findings that B. afzelii is the predominant species in the ROK [54,97]. Furthermore, our results were significantly lower than those reported in rodents in other countries: 24% in Austria [98], 16% in the Czech Republic [99], and 6.3% in Spain [100]. These differences in prevalence may be due to the tick vectors; the common tick vectors of Borrelia spp. in the ROK are Ixodes persulcatus, I. nipponensis, and I. granulatus [101]. B. afzelii is transmitted by I. ricinus and hosted by small mammals, and it is the most common causative agent of human LB [45,102]. The sequences from rodents showed 98.2–99.6% identity with those identified in ticks and humans in several countries. In the ROK, B. afzelii has been primarily reported in ticks [54,97,103] and rarely in humans [104]. Nevertheless, information on B. afzelii is still lacking. Although the infection rate of B. afzelii in rodents was the lowest, our findings suggest that B. afzelii may act as a causative agent of LB in the ROK.

This is the first report of C. burnetii in A. agrarius in the ROK. In this study, C. burnetii exhibited the second highest infection rate (16.0%). Nevertheless, our results were lower than those reported in China (18%) [105], Senegal (22.4%) [106], and Zambia (45%) [107] but higher than those reported in Brazil (4.6%) [93], Egypt (6.7%) [58], and Italy (1.4%) [61]. These differences may be explained by the rodent species and samples used for detection. In prior studies, C. burnetii detection was performed using various sample types such as blood, spleen, liver, and fecal samples. Consequently, the liver and spleen are considered suitable for the identification of C. burnetii. According to a previous study, the infection rate of C. burnetii in domestic livestock ranged from 6% to 22.7% depending on the species [57]. Although C. burnetii is a tick-borne pathogen, there are only a few reports of C. burnetii in ticks in the ROK [108,109]. Recent studies have reported co-infections of C. burnetii and SFTSV in ticks and humans [110, 111]; however, there was no co-infection with these two pathogens identified in rodents in this study. Despite the small number of R. norvegicus captured, C. burnetii infection was mostly detected in R. norvegicus; this could be because R. norvegicus may also serve as a reservoir in the ROK. A phylogenetic analysis based on the IS1111 gene revealed the presence of genetic variations within the sequences identified in A. agrarius. One sequence formed the same clade with the virulent strains reported in Brazil, whereas the other exhibited high similarity to strains reported in different countries. The disadvantage of the IS1111 gene is that it does not provide exact information, such as pathogenicity and species specificity (Fig 5); thus, we cannot draw any conclusions about what the separate groupings within these C. burnetii sequences might represent. Further research is necessary to determine the pathogenicity of C. burnetii circulating in the ROK. The results obtained in the present study suggest that A. agrarius plays a role in the transmission of C. burnetii in humans and animals.

Leptospira interrogans is a rodent-borne pathogen, and accordingly, it was the third most frequently detected (15.4%) in this study. Our results demonstrated a relatively high prevalence compared with that reported in previous studies [88,112]. This is the first time that Leptospira spp. have been investigated in rodents through sampling of extensive regions in the ROK. Compared with those reported in other countries, the infection rates ranged from 1.3% to 35.2% [113117]. R. norvegicus is also an important reservoir of this pathogen [72]; however, L. interrogans was detected in only one R. norvegicus and mostly detected in A. agrarius. Considering that R. norvegicus is commonly found around barns and farmhouses, this species also plays a critical role in the transmission of leptospirosis in domestic animals and humans. To date, L. interrogans has been divided into 23 serogroups based on serological methods and subdivided into more than 300 serovars [72]. The serovars circulating in each country are different, but the most frequently reported serovar worldwide is Icterohaemorrhagiae [72]. In the ROK, only a few studies have been conducted on serovar Lai [88, 118]. The phylogenetic analysis revealed that of the three sequences from rodents, two were classified as serovar Lai and one as serovar Manila, consistent with the findings from a previous study [88]. Consequently, Lai and Manilae are considered epidemic serovars in the ROK. The most important limitations of this study are that a serological analysis such as a microscopic agglutination test was not performed and that only a small number of samples were sequenced; therefore, serovar comparisons by province were not conducted. Although the number of the sequenced samples was low, the rpoB gene used in this study can be applicable for detection and serovar identification of L. interrogans. Furthermore, for accurate identification of L. interrogans serovars, serological testing along with the PCR method is absolutely necessary. These results suggest that the existence of various serovars in each province cannot be ruled out.

Since its first identification in China, SFTSV has been primarily detected in Asia [7478]. Due to its associated high mortality rate, there is significant interest in SFTSV [74,83,84]. In the present study, the infection rate of SFTSV in A. agrarius was 5.8%, and this is the first report to describe SFTSV infection in A. agrarius in the ROK. Our results were significantly lower than those reported in China (32.3%) [119]. Compared with the infection rates reported in other animals in the ROK, the prevalence of SFTSV in rodents was similar to that in wild boars (5.2%) [120] and ticks (6.0%) [121], but higher than that in cats (4.0%) [122], dogs (2.9%) [123], pigs (1.7%) [124], black goats (2.4%) [125], and wild animals (3.3%) [126]. However, the prevalence of SFTSV was the highest in feral cats (17.5%) in the ROK [127]. There has been a recent increase in the populations of feral cats, and they share habitats with wildlife, domestic animals, and humans. Several studies have demonstrated that SFTSV is transmitted to humans through direct contact with cats [128,129], suggesting that feral cats are infected by rodents. It is believed that SFTSV circulates in a zoonotic cycle between ticks and vertebrates [130]. Rodents are considered the representative reservoirs in maintaining tick-borne pathogens and may play a vital role in the transmission of SFTSV. The sequences obtained from A. agrarius belonged to subgenotype B-2 and D genotype; these results revealed a similar distribution in both genotypes. Sequences belonging to subgenotype B-2 are the most prevalent and associated with the highest mortality rate (43.8%) in the ROK [131], whereas genotype D is primarily found in China. Four sequences belonging to genotype D were identical to those found in a human patient in the ROK, suggesting that this genotype is pathogenic. Different genotypes of SFTSV have been shown to trigger different clinical manifestations in a ferret model [130]; however, although the clinical manifestations have not been confirmed in rodents, they may be pathogenic to humans. To date, SFTSV has been detected in diverse animals, but no conclusions can be drawn on how the virus is transmitted to these animals. The results of the present study provide a clue for elucidating the transmission route of SFTSV, suggesting the need to establish a continuous monitoring and surveillance systems to minimize a serious risk of SFTSV infection.

Conclusions

Urbanization and climate change affect not only on humans but also wildlife. The most significant concern caused by these changes is that the probability of disease transmission through ecosystem destruction has been significantly increasing compared with that observed in the past. This study investigated the prevalence of zoonotic pathogens in rodent populations through a systematic epidemiological investigation. Although we did not screen for all rodent-borne pathogens, the results indicated that, at least, rodents may act as critical reservoirs for A. phagocytophilum, Bartonella spp., B. afzelii, C. burnetii, L. interrogans, and SFTSV in the ROK. Our findings also demonstrated that rodents harbor several pathogens, implying the possibility of simultaneous transmission to humans. Most importantly, except for SFTSV, the pathogens investigated in this study are commonly misdiagnosed or underdiagnosed in the ROK; thus, their importance is neglected. Our findings indicate that rodents pose a potential risk to public health. Overall, our study provides useful information on rodent-borne pathogens and underscores the urgent need for rapid diagnosis, prevention, and control strategies for zoonotic diseases.

Supporting information

S1 Table. Number of captured rodents from each region in each province.

(DOCX)

pntd.0012306.s001.docx (20.7KB, docx)

Acknowledgments

We are very grateful to Dong-Hun Jang, Eun-Mi Kim, and Seung-Uk Shin for their valuable help in sample collection. All authors read and approved the final version.

Data Availability

All data generated during this study are included in the article and supplementary material. Raw sequencing files were deposited and are available in the repository, WEB LINK for A. phagocytophilum (https://www.ncbi.nlm.nih.gov/nuccore/OR287077.1, OR287091.1), for B. grahamii (https://www.ncbi.nlm.nih.gov/nuccore/OR288176.1, OR288190.1), for B. taylorii (https://www.ncbi.nlm.nih.gov/nuccore/OR288191.1, OR288193.1), for B. afzelii (https://www.ncbi.nlm.nih.gov/nuccore/OR284310.1, OR284311.1), for C. burnetii (https://www.ncbi.nlm.nih.gov/nuccore/OR284312.1, OR284321.1), for L. interrogans (https://www.ncbi.nlm.nih.gov/nuccore/OR284322.1, OR284324.1), and for SFTSV (https://www.ncbi.nlm.nih.gov/nuccore/OR257718.1, OR257726.1).

Funding Statement

The author(s) received no specific funding for this work.

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PLoS Negl Trop Dis. doi: 10.1371/journal.pntd.0012306.r001

Decision Letter 0

Amy C Morrison, Colleen B Jonsson

14 Mar 2024

Dear Dr. Choi,

Thank you very much for submitting your manuscript "Molecular surveillance of zoonotic pathogens from wild rodents in the Republic of Korea" for consideration at PLOS Neglected Tropical Diseases. As with all papers reviewed by the journal, your manuscript was reviewed by members of the editorial board and by several independent reviewers. In light of the reviews (below this email), we would like to invite the resubmission of a significantly-revised version that takes into account the reviewers' comments.

We cannot make any decision about publication until we have seen the revised manuscript and your response to the reviewers' comments. Your revised manuscript is also likely to be sent to reviewers for further evaluation.

When you are ready to resubmit, please upload the following:

[1] A letter containing a detailed list of your responses to the review comments and a description of the changes you have made in the manuscript. Please note while forming your response, if your article is accepted, you may have the opportunity to make the peer review history publicly available. The record will include editor decision letters (with reviews) and your responses to reviewer comments. If eligible, we will contact you to opt in or out.

[2] Two versions of the revised manuscript: one with either highlights or tracked changes denoting where the text has been changed; the other a clean version (uploaded as the manuscript file).

Important additional instructions are given below your reviewer comments.

Please prepare and submit your revised manuscript within 60 days. If you anticipate any delay, please let us know the expected resubmission date by replying to this email. Please note that revised manuscripts received after the 60-day due date may require evaluation and peer review similar to newly submitted manuscripts.

Thank you again for your submission. We hope that our editorial process has been constructive so far, and we welcome your feedback at any time. Please don't hesitate to contact us if you have any questions or comments.

Sincerely,

Colleen B Jonsson, PhD

Academic Editor

PLOS Neglected Tropical Diseases

Amy Morrison

Section Editor

PLOS Neglected Tropical Diseases

***********************

Reviewer's Responses to Questions

Key Review Criteria Required for Acceptance?

As you describe the new analyses required for acceptance, please consider the following:

Methods

-Are the objectives of the study clearly articulated with a clear testable hypothesis stated?

-Is the study design appropriate to address the stated objectives?

-Is the population clearly described and appropriate for the hypothesis being tested?

-Is the sample size sufficient to ensure adequate power to address the hypothesis being tested?

-Were correct statistical analysis used to support conclusions?

-Are there concerns about ethical or regulatory requirements being met?

Reviewer #1: There is some basic information that should be included in the methods.

1. the general description of “near rivers, valleys, farms, mountains, and lakes” is ambiguous. Were any other data collected (specific habitats, environmental conditions, etc)? Perhaps the authors could use more helpful descriptors (e.g., periurban? rural? near urban centers?) This would help their discussion, where they conclude that “rodents were trapped from areas with frequent movement of people, which may be associated with a high probability of disease transmission…” They state that the sites were selected by SFTS cases, but should provide more information to help understand what/where exactly they sampled, ecologically.

2. The authors must state how the rodents were identified. Defining how the rodents were identified becomes an issue as ~11% of the captured rodents were “unknown” species. Were the authors simply more confident in their identification of (the very distinctive) Apodemus agrarius and Rattus norvegicus, but were less confident to identify other rodents? If they identified A. agrarius as “rodent with a stripe” then they should state that as the identification method - how did they know it was not a Sicista sp? How did they discriminate between Rattus rattus and Rattus norvegicus?

3. The authors have to be more specific about their geographic scale. They refer to “province” in Tables 2 and 3, but display subdivisions of provinces in Figure 1. In the text they refer to “regions” and it seems region = province, but it is not clear. This should be very clearly defined, specifically stating the scale at which the data were analyzed, and explaining why the map shows a different scale than how the data were analyzed. For example, there appear to be 9 subdivisions of Gyeongbuk for which presence/absence is noted – are these the “regions” referred to in the text? Are these all regions that were sampled? Other examples: L276 – “Four regions” but 7 points are shown on Figure 1; L286 – “Five different regions” but 11 points are shown on Figure 1; L309 – “four different regions” but 6 points are shown on Figure 1; L330 – “found in all regions”.

4. One has to consider trapping effort for “prevalence” to be meaningful. The authors wish to make conclusions comparing the observed infection ratios between pathogens/regions/species and make comparisons to historical data (e.g., L226-L231, L232-L235 and Table 3). The probability of detecting something increases with increased sampling. For example, I would argue that there is very little that they can conclude about the vector/reservoir status of R. norvegicus based on 5 captures. So, in addition to the above mentioned points (describing the sampling sites and clarifying the geographic scale), the authors must state and/or consider the sampling effort (trap-nights per sampling unit, e.g., per site? region? province?) when analyzing their data. Otherwise they must limit their presentation, analysis, and discussion to presence/absence in the ROK.

5. If the authors define their sampling strategy and state their sampling effort with respect to geographic scale, they have to include correct statistical comparisons to make any inferences. For example, L259 – “The most” is misleading. Even though Bartonella were detected in 48% of A. agrarius, the confidence interval for the estimated number of R. norvegicus expected to be Bartonella-positive is ~1-70% based on 1/5 captures, i.e., there is no difference in infection ratio.

Reviewer #2: -Are the objectives of the study clearly articulated with a clear testable hypothesis stated? Yes

-Is the study design appropriate to address the stated objectives? Yes

-Is the population clearly described and appropriate for the hypothesis being tested? Yes

-Is the sample size sufficient to ensure adequate power to address the hypothesis being tested? Yes

-Were correct statistical analysis used to support conclusions? N/A

-Are there concerns about ethical or regulatory requirements being met? Yes

Reviewer comments were added to uploaded document.

Reviewer #3: - **Objectives and Hypothesis**: The objectives of the study are outlined but could be more explicitly connected to a clear, testable hypothesis. Clarifying the hypothesis would enhance the study's focus and provide a clearer framework for evaluation.

- **Study Design**: The design, involving molecular surveillance across various regions, appears appropriate for addressing the broad objectives related to pathogen prevalence. However, the justification for specific methodological choices (e.g., nested PCR) need to be strengthened.

- **Population Description**: The rodent population is clearly described, and the choice of species seems appropriate for the study's focus on zoonotic pathogens. The geographical and ecological breadth covered is a strength. Although the sample size is substantial for a surveillance study of this nature, a power analysis to justify the sample size in relation to expected pathogen prevalence is missing and would enhance the methodology.

- **Statistical Analysis**: There is minimal discussion on the statistical methods used for analyzing the data. Expanding on this, especially regarding the handling of co-infections and multiple comparisons, would support the conclusions drawn.

--------------------

Results

-Does the analysis presented match the analysis plan?

-Are the results clearly and completely presented?

-Are the figures (Tables, Images) of sufficient quality for clarity?

Reviewer #1: Table 3 – I suggest removing R. norvegicus from this table entirely. The status of the five specimens can be easily stated in the text. I think it is important to know which of the detections per province were from each species, and with 151 individuals, a Table is the best way to display the data for A. agrarius, but the R. norvegicus data makes these numbers ambiguous.

Reviewer #2: -Does the analysis presented match the analysis plan? Yes

-Are the results clearly and completely presented? No

-Are the figures (Tables, Images) of sufficient quality for clarity? Yes

Reviewer comments were added to uploaded document.

Reviewer #3: - **Clarity and Completeness**: The results are presented with significant findings regarding pathogen prevalence and co-infections. However, detailing in which tissues each pathogen was detected would provide a significant improvement.

- **Quality of Figures and Tables**: The provided figures and tables are adequate but could be enhanced for clarity, particularly regarding the visualization of co-infection patterns and their distribution across sampled regions.

--------------------

Conclusions

-Are the conclusions supported by the data presented?

-Are the limitations of analysis clearly described?

-Do the authors discuss how these data can be helpful to advance our understanding of the topic under study?

-Is public health relevance addressed?

Reviewer #1: The authors make conclusions concerning relative prevalence/occurrence of the rodents and pathogens with respect to geography. Without a more rigorous sampling strategy, or at least a better described/defined sampling scheme, they are limited in making some of these comparisons. In addition, the discussion includes details that are not completely relevant to the study design (as I have understood it). They should focus on presence/prevalence. They have no data on pathogenicity, so I recommend removing these points. I have included an edited pdf copy of the manuscript with my suggestions of things to delete for their consideration, and they could probably remove more.

The study has an additional limitation that should absolutely be addressed. The authors chose to use PCR or conventional RT-PCR for identification, yet failed to generate sequences from a proportion of the “positives”. The authors should address this specifically in the discussion: is this an acceptable ratio in similar studies? Should these be considered “putative” positive? Why weren’t more sensitive and specific methods used (e.g., RTqPCR)? Could this also influence the ratio when comparing to other, previously published molecular surveys (e.g., Kim et al. 2022 Parasite & Vectors 15:486, doi: 10.1186/s13071-022-05608-w)?

Another minor limitation that the authors should address is that they provide no information about the structure of the cohort (males/females, adult/juvenile, etc). This is not completely necessary to include in the analysis, but should be mentioned/considered in the discussion as it may affect the observed prevalence (infection ratio); and I suspect it had a very large affect on the trapping success.

Reviewer #2: -Are the conclusions supported by the data presented? Yes

-Are the limitations of analysis clearly described? Yes

-Do the authors discuss how these data can be helpful to advance our understanding of the topic under study? Yes

-Is public health relevance addressed? Yes

Reviewer comments were added to uploaded document.

Reviewer #3: - **Support by Data**: The conclusions drawn about the prevalence and public health significance of the detected pathogens are generally supported by the data, albeit with the caveat that the methodological limitations could impact these findings.

- **Limitations**: The discussion of limitations, especially regarding methodological choices (nested PCR, partial genome sequencing), is needed. Acknowledging these could strengthen the study's credibility.

- **Advancement of Understanding**: The manuscript makes a valuable contribution by mapping zoonotic pathogen prevalence in rodents in the ROK.

--------------------

Editorial and Data Presentation Modifications?

Use this section for editorial suggestions as well as relatively minor modifications of existing data that would enhance clarity. If the only modifications needed are minor and/or editorial, you may wish to recommend “Minor Revision” or “Accept”.

Reviewer #1: (No Response)

Reviewer #2: Reviewer comments were added to uploaded document.

Reviewer #3: (No Response)

--------------------

Summary and General Comments

Use this section to provide overall comments, discuss strengths/weaknesses of the study, novelty, significance, general execution and scholarship. You may also include additional comments for the author, including concerns about dual publication, research ethics, or publication ethics. If requesting major revision, please articulate the new experiments that are needed.

Reviewer #1: The authors screen for the presence of some bacterial pathogens and one arbovirus in 2 rodent species captured at targeted sites, based on human cases of the arbovirus. The main goal was to characterize the presence of these zoonotic pathogens in the Republic of Korea in two rodent species. They screen by molecular diagnostic methods, and report the infection ratios by species and by geographic unit. They also included some phylogenetic analyses of the detected pathogens, including some (but not all) of the "positives". Overall the methods require a bit more clarification, because I think the manuscript needs a better perspective on what can/not be inferred from the study design and data. As explained in other comments above, the geographic unit and sampling effort need to be clearly defined if the authors wish to infer prevalence based on geography. The phylogenetic analysis is fine, but the authors should limit the conclusions they can make from these data concerning pathogenicity. Simply stated, this could be a simple epidemiological survey for multiple pathogens. However, the authors could make some additional inferences (e.g., geographic distribution) if they are more scientific about the approach. Therefore, the discussion needs major revision, and that will depend on if/how the authors improve the methods.

In addition to the major points mentioned above, here are some minor suggestions / clarifications that would help the mansucript:

L135-L136: SFTSV was only briefly Huaiyangshan banyangvirus, has been Dabie bandavirus since 2018, and is now Bandavirus dabieense according to ICTV

L147 – I would rephrase this as “…rodents may be involved in the transmission cycles of various diseases.” Particularly as this is the hypothesis they intend to investigate.

L153 “…to investigate the occurrence of some rodent-borne diseases…”

L222 – I am confused by this sentence. I was under the impression that the authors only captured rodents in the ROK, but here they state that A. agrarius was captured “mostly” in ROK (and also somewhere else?). Perhaps the authors mean that A. agrarius was found at all sites (?) but R. norvegicus was only captured at 2 sites? Two regions?

L172 – define “serum separating tube (SST)”

L267 – “…formed the same group as B. grahamii found in leeches (KX270012) and found in A. agrarius (JN810851) reported in the ROK…”

L279 and Figure 1 – B. burgdorferi is listed in the figure but the phylogenetic analysis in Figure 4 and text L279 state that this is B. afzelii. Please clarify in the text or write “B. burgdorferi s.l.” on the figure.

L292-293 what was

Attachment

Submitted filename: PNTD-D-23-00918_reviewerA.pdf

pntd.0012306.s002.pdf (2.4MB, pdf)
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Submitted filename: Reviewer Comments.docx

pntd.0012306.s003.docx (12.8KB, docx)
PLoS Negl Trop Dis. doi: 10.1371/journal.pntd.0012306.r003

Decision Letter 1

Amy C Morrison, Colleen B Jonsson

13 May 2024

Dear Dr. Choi,

Thank you very much for submitting your manuscript "Molecular surveillance of zoonotic pathogens from wild rodents in the Republic of Korea" for consideration at PLOS Neglected Tropical Diseases. As with all papers reviewed by the journal, your manuscript was reviewed by members of the editorial board and by several independent reviewers. The reviewers appreciated the attention to an important topic. Based on the reviews, we are likely to accept this manuscript for publication, providing that you modify the manuscript according to the review recommendations.

Please prepare and submit your revised manuscript within 30 days. If you anticipate any delay, please let us know the expected resubmission date by replying to this email.

When you are ready to resubmit, please upload the following:

[1] A letter containing a detailed list of your responses to all review comments, and a description of the changes you have made in the manuscript.

Please note while forming your response, if your article is accepted, you may have the opportunity to make the peer review history publicly available. The record will include editor decision letters (with reviews) and your responses to reviewer comments. If eligible, we will contact you to opt in or out

[2] Two versions of the revised manuscript: one with either highlights or tracked changes denoting where the text has been changed; the other a clean version (uploaded as the manuscript file).

Important additional instructions are given below your reviewer comments.

Thank you again for your submission to our journal. We hope that our editorial process has been constructive so far, and we welcome your feedback at any time. Please don't hesitate to contact us if you have any questions or comments.

Sincerely,

Colleen B Jonsson, PhD

Academic Editor

PLOS Neglected Tropical Diseases

Amy Morrison

Section Editor

PLOS Neglected Tropical Diseases

***********************

Reviewer's Responses to Questions

Key Review Criteria Required for Acceptance?

As you describe the new analyses required for acceptance, please consider the following:

Methods

-Are the objectives of the study clearly articulated with a clear testable hypothesis stated?

-Is the study design appropriate to address the stated objectives?

-Is the population clearly described and appropriate for the hypothesis being tested?

-Is the sample size sufficient to ensure adequate power to address the hypothesis being tested?

-Were correct statistical analysis used to support conclusions?

-Are there concerns about ethical or regulatory requirements being met?

Reviewer #1: The authors have improved the methods description by now including a table with regions sampled within provinces, as well as defining ecological categories that describe each region. They added more information, but there the sampling effort is still ambiguous. The authors must be very clear about trap effort. Per the methods, they define 1 trap-night = 60 traps. *State how many trap-nights were performed in each region.*

Reviewer #2: Line 173-178 – Please clarify, was each capture location only sampled once or were they sampled multiple times?

--------------------

Results

-Does the analysis presented match the analysis plan?

-Are the results clearly and completely presented?

-Are the figures (Tables, Images) of sufficient quality for clarity?

Reviewer #1: L316 (previously L293) The authors have included bootstrap values on the phylogenetic trees. However, they did not answer my previous question concerning the use of the word "clades". How were the clades defined? The authors state “there are several clades” – how did they define these clades? There do not seem to be any “clades” in Figure 5 and I wonder why/how one could describe genetic variability (or define clades) with a 203 bp segment. The best solution would be to remove the mention of “clades”. There are specific methods for defining genetic clusters (not necessarily high bootstrap support), and those methods were not used in the manuscript. This is a minor point, and it is only a suggestion for improvement, as many people write “clades” or “clusters” without such formal analysis. I was confused about their responses about this, so I thought I would mention it again.

Reviewer #2: Figure 6 – Please state what the box of dash line indicates.

Line 370 – Please add citation for statement about difference in sensitivity by nested-PCR and qPCR.

Line 373 – Please elaborate what is meant by “sequences were poor.”

--------------------

Conclusions

-Are the conclusions supported by the data presented?

-Are the limitations of analysis clearly described?

-Do the authors discuss how these data can be helpful to advance our understanding of the topic under study?

-Is public health relevance addressed?

Reviewer #1: The authors have not addressed the issue of PCR-positive/negative. They have included information about how many sequences were “selected” for analysis (209-210), but that is clearly not true, nor is it helpful resolving the issue raised previously. For example, clearly all 15 “successfully” sequenced A. phagocytophilum were included in Figure 2, and not “<5” as stated in the methods. Regardless, the issue is whether “unsuccessful” sequencing of a PCR product means that the sample is negative. The authors attempted to address these limitations in the discussion (paragraph beginning L369), but they have not addressed the issue of false-positivity.

I disagree with their statement that nested PCR is more sensitive and specific than qPCR (L369), and I would counter that nested PCR is more prone to false-positive results, and therefore less specific. The classical way to confirm conventional PCR (positivity and specificity) is to sequence the resulting amplicons. Otherwise, the samples should be considered putatively/potentially positive. The authors clearly state that 15 of 21 Anaplasma-positive (L269), 15 of 78 Bartonella-positives (L284), 2 of 5 Borellia-positives, etc were *successfully* sequenced. That is a significant proportion of PCR-positives. They mentioned that sequencing was not successful in the discussion (L431, L483). That is a huge "red flag" that those were not true positives.

The explanations the authors provide in the discussion (a “low density infection” or the fact that the primers do not match some Leptospira serovars) are unclear and create some additional problems.

The way to resolve this, as I suggested last time as well, is for the authors to state in the discussion that they considered PCR-positives to be truly positive, regardless of whether the amplicon could be sequenced, and note that this may overestimate the number of true positives, as some amplicons could not be sequenced. I suggest that they do not speculate that it is due to a “low density infection” (L431), and they do not imply that their PCR was inefficient (L483).

Reviewer #2: (No Response)

--------------------

Editorial and Data Presentation Modifications?

Use this section for editorial suggestions as well as relatively minor modifications of existing data that would enhance clarity. If the only modifications needed are minor and/or editorial, you may wish to recommend “Minor Revision” or “Accept”.

Reviewer #1: L136 It is worth revising this more precisely. The virus is still called “severe fever with thrombocytopenia syndrome virus” and should still be called that. However, the official scientific name is Bandavirus dabieense. Just like the “striped field mouse” is Apodemus agrarius.

L255 correct the spelling of SFTSV

Reviewer #2: (No Response)

--------------------

Summary and General Comments

Use this section to provide overall comments, discuss strengths/weaknesses of the study, novelty, significance, general execution and scholarship. You may also include additional comments for the author, including concerns about dual publication, research ethics, or publication ethics. If requesting major revision, please articulate the new experiments that are needed.

Reviewer #1: The authors have made many improvements to the manuscript. I think there are still a few minor points that should be corrected.

There are also some changes in the revision that I disagree with. I do not agree with the complete removal of information regarding unidentified rodents. It makes sense to concentrate the study on one species for the manuscript. However, I would expect that one would collect a variety of species using their stated trapping method. It now seems as though the authors only captured two species. This is suspicious and unlikely.

I do not agree with completely removing the pathogen-detection results from R norvegicus. My previous comments were intended to help clarify the data presentation and analysis, I was not suggesting the authors censor their data. Now it seems strange that the manuscript refers to pathogens in “rodents”, when, actually, the authors only present data from A agrarius. It is also strange that they state only 156 rodents were captured (which is untrue), list two species that they could identify, and then remove R norvegicus from the analysis.

There are two alternatives, as I see it: they state how many rodents were captured in total (175), and then state that this study focused on identifying human pathogens in the 151 A. agrarius (86%). Don't mention any other species at all.

Alternatively, they should return the results to how it was written originally: "A total of 175 rodents were captured and morphologically classified as follows: Apodemus agrarius (striped field mouse) (n = 151), Rattus norvegicus (Norway rat) (n = 5), and unknown (n = 19)." This was completely fine. My original comment was that including all rodents in the table was confusing. As there were only 5 brown rats, they could have simply stated these results in the respective sections (e.g., "Bartonella was detected in 3 brown rats").

Reviewer #2: Please find below minor points and suggestions that may help.

Line 42 – Is the author’s suggestion for the ROK or worldwide as it known that rodents harbor various pathogens?

Line 148-149 – Sentence construction and word choice

Line 269 – “indicating that this pathogen was spread throughout the ROK.”

Line 345 – Suggest removing the word potentially as the pathogens characterized in the manuscript are zoonotic pathogens.

Line 407-410 – Please clarify sentence and the point the author is conveying.

Line 1020 – Sentence construction and suggest the use of the word symbol instead of markings.

--------------------

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Reviewer #2: No

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PLoS Negl Trop Dis. doi: 10.1371/journal.pntd.0012306.r005

Decision Letter 2

Amy C Morrison, Colleen B Jonsson

21 Jun 2024

Dear Dr. Choi,

We are pleased to inform you that your manuscript 'Molecular surveillance of zoonotic pathogens from wild rodents in the Republic of Korea' has been provisionally accepted for publication in PLOS Neglected Tropical Diseases.

Before your manuscript can be formally accepted you will need to complete some formatting changes, which you will receive in a follow up email. A member of our team will be in touch with a set of requests.

Please note that your manuscript will not be scheduled for publication until you have made the required changes, so a swift response is appreciated.

IMPORTANT: The editorial review process is now complete. PLOS will only permit corrections to spelling, formatting or significant scientific errors from this point onwards. Requests for major changes, or any which affect the scientific understanding of your work, will cause delays to the publication date of your manuscript.

Should you, your institution's press office or the journal office choose to press release your paper, you will automatically be opted out of early publication. We ask that you notify us now if you or your institution is planning to press release the article. All press must be co-ordinated with PLOS.

Thank you again for supporting Open Access publishing; we are looking forward to publishing your work in PLOS Neglected Tropical Diseases.

Best regards,

Colleen B Jonsson, PhD

Academic Editor

PLOS Neglected Tropical Diseases

Amy Morrison

Section Editor

PLOS Neglected Tropical Diseases

***********************************************************

PLoS Negl Trop Dis. doi: 10.1371/journal.pntd.0012306.r006

Acceptance letter

Amy C Morrison, Colleen B Jonsson

3 Jul 2024

Dear Dr. Choi,

We are delighted to inform you that your manuscript, "Molecular surveillance of zoonotic pathogens from wild rodents in the Republic of Korea," has been formally accepted for publication in PLOS Neglected Tropical Diseases.

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Associated Data

    This section collects any data citations, data availability statements, or supplementary materials included in this article.

    Supplementary Materials

    S1 Table. Number of captured rodents from each region in each province.

    (DOCX)

    pntd.0012306.s001.docx (20.7KB, docx)
    Attachment

    Submitted filename: PNTD-D-23-00918_reviewerA.pdf

    pntd.0012306.s002.pdf (2.4MB, pdf)
    Attachment

    Submitted filename: Reviewer Comments.docx

    pntd.0012306.s003.docx (12.8KB, docx)
    Attachment

    Submitted filename: Response to reviewers comments.docx

    pntd.0012306.s004.docx (30.5KB, docx)
    Attachment

    Submitted filename: Response to reviewers comments.docx

    pntd.0012306.s005.docx (21.3KB, docx)

    Data Availability Statement

    All data generated during this study are included in the article and supplementary material. Raw sequencing files were deposited and are available in the repository, WEB LINK for A. phagocytophilum (https://www.ncbi.nlm.nih.gov/nuccore/OR287077.1, OR287091.1), for B. grahamii (https://www.ncbi.nlm.nih.gov/nuccore/OR288176.1, OR288190.1), for B. taylorii (https://www.ncbi.nlm.nih.gov/nuccore/OR288191.1, OR288193.1), for B. afzelii (https://www.ncbi.nlm.nih.gov/nuccore/OR284310.1, OR284311.1), for C. burnetii (https://www.ncbi.nlm.nih.gov/nuccore/OR284312.1, OR284321.1), for L. interrogans (https://www.ncbi.nlm.nih.gov/nuccore/OR284322.1, OR284324.1), and for SFTSV (https://www.ncbi.nlm.nih.gov/nuccore/OR257718.1, OR257726.1).


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