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Article

Geographical Distribution of Mauremys sinensis, Mauremys reevesii, and Their Hybrids in South Korea

by
Hae-Jun Baek
1,*,
Eujin Cheong
2,
Youngha Kim
3,
Kyo Soung Koo
4,
Su-Hwan Kim
5,
Chang-Deuk Park
6 and
Ju-Duk Yoon
6
1
Invasive Alien Species Team, Bureau of Survey and Safety Research, National Institute of Ecology, Seocheon 33657, Republic of Korea
2
National Migratory Birds Center, National Institute of Biological Resources, Incheon 22689, Republic of Korea
3
National Ecosystem Survey Team, Bureau of Survey and Safety Research, National Institute of Ecology, Seocheon 33657, Republic of Korea
4
Korean Environmental Geography Institute, Sejong 30141, Republic of Korea
5
Wetland Research Team, Wetland Center, National Institute of Ecology (NIE), Changnyeong 50303, Republic of Korea
6
Research Center for Endangered Species, National Institute of Ecology (NIE), Yeongyang 36531, Republic of Korea
*
Author to whom correspondence should be addressed.
Animals 2024, 14(18), 2626; https://doi.org/10.3390/ani14182626
Submission received: 12 August 2024 / Revised: 4 September 2024 / Accepted: 6 September 2024 / Published: 10 September 2024
(This article belongs to the Section Ecology and Conservation)
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Abstract

:

Simple Summary

The global economic cost of managing invasive species exceeded $423 billion annually in 2019 and has increased at least fourfold every decade since 1970. In South Korea, the annual damage caused by invasive species is estimated to be between $93 million and $51.68 million. South Korea is vulnerable to invasive species and the cost of invasive species is estimated to be the highest among other countries, indicating the need for policy measures and responses. Most of the invasive reptiles in South Korea are introduced and released by humans. The hybridization of the Chinese striped-necked turtle Mauremys sinensis and Reeves’ turtle M. reevesii identified in the current study is also suspected to have been introduced from captivity into the wild, raising alarm bells. This suggests that the introduction of hybrids into the wild could pose a serious problem for biodiversity, especially for the M. reevesii, as it could undermine the genetic diversity of the population. Public awareness and education are needed to preserve South Korea’s biodiversity, and efforts must be made to reduce the number of exotic reptiles introduced into the wild.

Abstract

The Chinese striped-necked turtle Mauremys sinensis, introduced into South Korea presumably in 2012, is considered an invasive alien species owing to its devastating impact, including hybridization with the native protected species Reeves’ turtle M. reevesii. Recently, the presence of M. sinensis has been confirmed throughout the country, and several sympatric areas with M. reevesii have been reported. Thus, field surveys were conducted at 47 sites across M. sinensis and M. reevesii habitats in South Korea to determine the extent of hybridization. Five sympatric sites were confirmed, and hybrid individuals were identified at four sites. Genetic analyses (COI and R35) of two individuals from Jeju Island confirmed maternal M. reevesii and paternal M. sinensis lineages. Hybridization presumably does not occur under natural conditions, and the hybrids likely originated from captive breeding. This study identifies for the first time the habitats of M. sinensis and its hybrids in the wild of South Korea. The management measures proposed in the current study could be of value for the conservation of the native species; however, our study did not include reproductive monitoring, and there is a need for such surveys as well as for systematic management of non-native turtles introduced into South Korea.

1. Introduction

Alien species in South Korea are classified as Invasive Alien Species (IAS), based on their potential for introduction, establishment and spread; their impact on ecosystems, society and the economy; and the difficulty of biological control. To date, five species of invasive alien turtles have been recorded, Pseudemys concinna, Pseudemys nelsoni, Mauremys sinensis, Macrochelys temminckii, Chelydra serpentina, and all species of the genus Trachemys [1]. The exact purpose of importation of non-native turtles is not known, but it is assumed that most are imported as pets [2,3,4,5].
One of the IAS of turtles, the Chinese striped-necked turtle Mauremys sinensis (order Testudines; family: Geoemydidae), is listed as “Endangered” in the IUCN Red List [6] and in CITES Appendix III [7]. This species is native to mainland China (Fujian, Guangdong, Guangxi, Hainan and Zhejiang Provinces), Taiwan and Vietnam and has been introduced to South Korea, the United States (Florida), Europe and Japan [8]. Although the specific dates and intentions of these introductions remain unconfirmed, M. sinensis may have been imported as an alternative to Trachemys spp. (red-eared sliders), which were banned from import and distribution when they were designated as IAS in 2001 [9].
Mauremys sinensis, a globally traded species, was identified in the wild in South Korea in 2012 [10], and its establishment in the country was confirmed in 2016 [11]. Adult M. sinensis individuals are approximately 25 cm long, and females grow larger than males [9]. Their recorded maximum lifespan is 22.8 years in captivity, and they are omnivorous with distinct prey preferences between males and females—adult females are omnivorous with a notable herbivorous preference, whereas adult males and young individuals are predominantly carnivorous [9].
Species of the Geoemydidae family frequently exhibit interspecific (and intrageneric) hybridization, which commonly occurs in captive settings. The release of such hybrids into the wild poses a substantial risk of introgression, potentially leading to the loss of unique genetic traits of wild populations. According to Stuart and Parham [12], 14 new Geoemydidae species have been reported in the past 20 years, 6 of which originated from hybridization in captivity. Mauremys sinensis hybridizes with congeneric species, resulting in hybrids such as M. sinensis × M. reevesii, M. sinensis × M. annamensis, and M. sinensis × C. trifasciata [13,14,15].
The semi-aquatic Reeves’ turtle M. reevesii is native to South Korea; it is protected by law, such as Natural Monument No. 453, and is listed as Endangered Wildlife II in South Korea [16]. Adults of the species can grow up to 30 cm in length [17]. This species can be distinguished from M. sinensis by its dark brown carapace with three ridges and a lemon-yellow, C-shaped patch on the side of its face. Habitat loss and destruction severely reduced the distribution of M. reevesii, and the recent introduction of non-native turtle species such as M. sinensis into its range, with potential for hybridization, has exacerbated the already precarious situation of M. reevesii [2,9,18,19,20,21].
There are no studies on M. sinensis or hybrids of M. sinensis and M. reevesii in South Korea, and there is a need to determine the distribution of these species in South Korea and the existence of hybrid individuals in the wild. This is essential for the development of effective conservation strategies for native protected species M. reevesii, as well as priority management points and targets for invasive species. Therefore, in the present study, we aimed to identify the current habitats of M. sinensis and M. reevesii and to establish an accurate genetic analysis method for species identification.

2. Materials and Methods

2.1. Distribution of M. sinensis, M. reevesii and Their Hybrids

To determine the distribution status of M. sinensis, M. reevesii and their hybrids in South Korea, a comprehensive literature review and field surveys were conducted from 2017 to 2022. Survey sites were selected based on the reports of the National Institute of Ecology, namely the “Nationwide Survey of Non-native Species in Korea from 2016 to 2021” [2,3,18,19,20] and the 2018 report “Investigating Ecological Risk of Alien Species”.
As a result of the distribution check, 48 distribution sites of M. sinensis and M. reevesii were identified, and among them, two hybrid individuals were identified in captivity at one breeding facility located in Hwaseong, Gyeonggi-do (Table 1, No. 48). Based on the results, we conducted field surveys at 47 sites identified in the literature to confirm the outdoor distribution of M. sinensis and M. reevesii hybrids in the wild. The sites were mainly urban ecological parks and included reservoirs and rivers near schools and religious institutions. Taking advantage of freshwater turtles’ habit of basking to maintain body temperature, surveys were mainly conducted between 11 am and 4 pm. Field surveys were conducted using a pair of binoculars (SLC 8 × 42 WBHD; Swarovski, Absam, Austria) and a field scope (ATM 65HD; Swarovski). Individuals identified during field surveys were initially identified in the field based on the shape and number of lateral facial lines and the shape and color of the carapace; final species determination was made after photographical confirmation. The survey was conducted as part of the 2022–2023 project of the National Institute of Ecology ‘Monitoring of Invasive Alien Species’ project.

2.2. Hybrid Specimen Sampling

Captive surveys were conducted in 2021–2022 to collect samples for genetic analysis at seven sites (Table 1, sites 26, 38, 43–47), including four sites where hybridization had been identified through the literature and fieldwork. Turtles were captured using floating traps. The traps were made of transparent acrylic material measuring 70 cm × 70 cm, with a depth of 20 cm, and Japanese sardinella (fish) or pork was used as bait. Of the turtles collected during the survey, IAS turtles were euthanized in accordance with the Korean Biodiversity Act, hybrids (M. sinensis × M. reevesii) and M. reevesii were released after blood sampling, and non-study species were released without sampling.
In addition, an M. reevesii breeding farm in South Korea (Table 1, no. 48) was visited to collect blood samples from two individuals suspected of being subjected to hybridization in the breeding facility. Less than 2 mL blood was collected for genetic analysis from the captured individuals; M. sinensis and hybrids were transported to the laboratory and killed, whereas M. reevesii individuals were released back into the field.
A total of thirteen individuals of M. sinensis, M. reevesii and their hybrids were collected during field surveys and visits to captive breeding facility, with three individuals of M. sinensis (Tor019, 020, and 410), six individuals of M. reevesii (Tor409, 411, 412, 413, 414, and 415), and four individuals of their hybrids (Tor036, 037, 062, and 274). The survey was conducted as part of the 2022–2023 project of the National Institute of Ecology ‘Monitoring of Invasive Alien Species’ project.

2.3. Genetic Analysis

DNA was extracted using a Qiagen DNeasy Blood and Tissue kit (Qiagen, Hilden, Germany) following the manufacturer’s instructions. For molecular identification, the mitochondrial DNA cytochrome c oxidase subunit I (COI) gene and nuclear DNA R35 gene were targeted, and novel primers were designed to amplify the target regions: the COI region was amplified using MAU-MT-CO1-05190f (5′-TARTTAACAGCTAAAYACCC-3′) and MAU-MT-CO1-07039r (5′-AACCTATAATYTAACCTTGACAA-3′); for sequencing, MAU-MT-CO1-05831f (5′-TAACTATCTTTTCCCTYCACCTA-3′) was used. The R35 region of nuclear DNA intron 1 was amplified using MAU-R35-1f (5′-CAAAAGTCATTCTCTGGCTTC-3′), MAU-R35-2f (5′-GTCAGACTTCTTTGCATATTTGTAA-3′), and MAU-R35-1r (5′-CAACTATGTGCTGGACAG-3′). AccuPower PCR PreMix (BIONEER, Daejeon, Republic of Korea) was used for both amplification reactions, and 20 ng of genomic DNA was obtained from a reaction mixture of 20 µL. Polymerase chain reaction (PCR) conditions were as follows: 5 min at 95 °C for initial denaturation, 30 cycles for 20 s at 95 °C, 20 s at 55 °C, 2 min at 72 °C, and final elongation for 5 min at 72 °C. All samples were purified using an AccuPrep PCR Purification Kit (BIONEER) and sequenced on an ABI3730XL system (Applied Biosystems, Waltham, MA, USA) following the manufacturer’s instructions.
The sequences of the COI and R35 fragments were edited and aligned using Geneious 5.3.6 (BIOMATTERS, Auckland, New Zealand). Multiple-sequence alignments were performed using CLUSTAL X [22]. Pairwise sequence divergence within and between Mauremys species was estimated using MEGA version 7 [23]. SeqPHASE (https://eeg-ebe.github.io/SeqPHASE/, accessed date: 11 August 2024) [24] was used to confirm the alleles of the parental species.
DNA molecular phylogenies were reconstructed using the maximum likelihood method with default priors and 1000 bootstrap replicates using MEGA version 7 [24] and the best-fit model for sequence evolution was selected using the same software. For the best-fit models, 24 different nucleotide substitution models were compared and the models with the lowest BIC (Bayesian information criterion) scores were considered to best describe the substitution pattern. The best-fit model for COI based on the Bayesian information criterion was the T92 + G model and that for R35 was the T92 + G + I model. To ensure accurate construction of the phylogenetic trees, 12 sequences of M. sinensis, 6 sequences of M. reevesii, 3 sequences of Mauremys japonica, and 5 sequences of Mauremys mutica were used, and Cuora aurocapitata (NCBI GenBank accession AY874540) and C. amboinensis (accession NC_014769) were used as outgroups.

2.4. Compliance with Ethical Standards

No animals were harmed, no drugs were used, and a small amount of blood was collected from a blood vessel. No animals were euthanized to collect blood samples nor was any physical harm done to the animals. Samples for molecular studies were obtained from the turtles’ tail veins. However, M. sinensis (IAS for South Korea) were euthanized in accordance with South Korea’s “Act on the Conservation and Use of Biological Diversity,” and part of the tail muscle was used.

3. Results

3.1. Distribution of M. sinensis, M. reevesii and Their Hybrid

We confirmed the presence of M. sinensis, M. reevesii and their hybrid at 47 sites across South Korea (Table 1, Figure 1), and a total of 143 individuals were examined. At five of these sites, M. sinensis and M. reevesii cooccurred, and a hybrid individual occurred at four sites. The sympatric sites for the two species were Daejeon (Chimsan-dong), Nonsan (Cheonggok-ri), Ulju (Cheonsang-gil), Jinju (Jangsari) and Jeonju (Kwon Samdeok-ro), and a hybrid individual was identified in Jeonju, Yeosu, Jeju and Seogwipo (Table 1, no. 44–47). Hybridization of M. sinensis with M. reevesii was confirmed at four sites: Jeonju (Kwon Samdeok-ro), Yeosu City (Hakdong), Jeju City (Gwangnyeong-ri) and Seogwipo City (Namjung-ro). Mauremys sinensis was confirmed at 33 sites with 68 individuals in total, whereas M. reevesii occurred at only 16 sites with 66 individuals. In addition, seven hybrids of M. sinensis and M. reevesii were found in four sites. Most individuals of M. sinensis were observed in Busan (Choeupcheon-dong, Table 1, no. 21) and M. reevesii in Gurye (Gurye-eup, Table 1, no. 38). The number of individuals found by species was similar for M. sinensis and M. reevesii, but the distribution of M. sinensis was about twice that of M. reevesii, which was judged to be due to the variety of human release sites and the limited number of individuals reared by humans, rather than natural reproduction. In addition, M. sinensis was mainly found in urban ecological parks with high human traffic, whereas M. reevesii was more frequent in less-disturbed, natural habitats.

3.2. Occurrence of M. sinensis × M. reevesii Hybrid

Turtle traps were mounted at seven sites, and nine turtles were captured at four sites (Table 1, Figure 2). Five individuals of M. reevesii were captured in Gurye-gun (Gurye-eup, Table 1, no. 38), two individuals of M. sinensis were captured in Busan (Hadan-dong, Table 1, no. 26), and two hybrid individuals were captured in Jeju Island (Gwangnyeong-ro, Namseongjung-ro, Table 1, nos. 46–47), where hybridization of M. sinensis and M. reevesii was confirmed. In addition, blood samples from two hybrid individuals and one each from M. sinensis and M. reevesii were collected from the M. reevesii breeding farm.

3.3. Phylogenetic Analyses

The nine individuals captured in turtle traps and the four captive individuals were used for phylogenetic analysis. A total of 24 sequences (11 from GenBank, including sequences of 2 outgroups of the genus Cuora) were included for COI analysis and 31 sequences (18 from GenBank) were included for R35 analysis. The partial sequence (615 bp) of mtDNA COI from the 13 specimens represented two distinct clades in the maximum likelihood reconstruction (Figure 3). The pairwise sequence divergence among different clades ranged from 3.6% ± 0.7% to 4.4% ± 0.8%, and the overall sequence divergence was 2.6% ± 0.4%. The four suspected hybrids (Tor 036, 037, 062, and 274) belonged to the M. sinensis and M. reevesii clades. Tor 036 belonged to M. sinensis, whereas as all other suspected hybrids belonged to M. reevesii. The 13 sequences from the same sample as COI comprised two separate clades: M. sinensis and M. reevesii (Figure 4). The overall sequence divergence was 0.5% ± 0.1%, and that among Mauremys species ranged from 0.4% ± 0.1% to 1.1% ± 0.3%. All suspected hybrid individuals possessed both M. sinensis and M. reevesii alleles, indicating that they originated from independent hybridization events.

4. Discussion

In the current study, we verified the occurrence of M. sinensis in South Korea, its sympatric areas with M. reevesii, and the first record of hybridization between M. sinensis and M. reevesii in the wild. Seven hybrids of M. reevesii and M. sinensis were identified by field observation at four sites, and genetic analysis of two of the hybrids collected on Jeju Island revealed the maternal lineage as M. reevesii and the paternal lineage as M. sinensis.
To date, no breeding studies of these hybrids have been conducted in South Korea, and it is uncertain whether the hybrid individuals identified in the wild are naturally occurring or released from captivity. However, of the four sites where hybrid individuals have been identified, no individuals of M. sinensis or M. reevesii have been observed by census or collection surveys, except for Jeonju (Table 1, no. 44), and no hybrid individuals have been identified in the remaining five sites where M. sinensis and M. reevesii co-occurrence was observed, except for Jeonju, so it is likely that the hybrid individuals identified in the field to date have been released from captivity.
The only non-native turtles that have been confirmed to breed in South Korea are Trachemys scripta, Pseudemys spp. and Chelydra serpentina, and no other non-native species have been confirmed to breed [25,26,27,28]. In particular, no native turtle species other than Pelodicus maackii have been reported on Jeju Island, where the hybrid individuals were collected, and five alien turtle species (Trachemys scripta, Pseudemys concinna, Pseudemys nelsoni, Mauremys sinensis and Podocnemis unifilis) have been observed [3,29]. Therefore, we are certain that the hybrids identified on Jeju Island are captive-bred individuals. However, detailed breeding studies should be conducted in public areas and hybridization sites to confirm wild breeding. It is also noted that the genetic introgression of hybrids found in the wild should be investigated through more detailed surveys.
Studies on the potential effects of non-native turtles on native turtle populations [30,31,32] have confirmed overlapping ecological niches in terms of food sources and behavioral ranges. Non-native species disrupt native species diversity through competition, disease transmission and hybridization with native species. They also increase the risk of native species extinction and cause changes in ecosystem functions and service delivery [33]. Therefore, Deokjin Lake in Jeonju City, where both M. sinensis and M. reevesii and their hybrids were identified in current study, should be designated as a priority intensive management area for more aggressive removal of invasive alien turtles and habitat restoration. During the nesting season, it is recommended that nest destruction and capture surveys of turtles coming ashore should be carried out, as well as permanent capture surveys using floating traps that take advantage of the behavior of turtles basking in the sun. Park et al. [34] found that it would be beneficial to manage abandoned individuals in captivity to prevent natural release and save management costs after abandonment. Therefore, efforts such as free collection services for abandoned invasive turtles or the designation of dumping sites in urban ecological parks, where invasive turtles are commonly found, will be necessary to prevent their release into the wild.
Over the past 20 years, 161 tons of turtles have been imported into South Korea from 63 countries [1]. China, the origin of M. sinensis, is the largest domestic importer of turtles, with approximately 110 tons imported in the past two decades. The turtle industry in China is extensive, with as many as 10 turtle farms in Hainan alone and different species of turtles reared in the same ponds [35]. Indeed, M. iversoni (invalid taxon) has also been identified as a hybrid arising from co-rearing of M. mutica and C. trifasciata on turtle farms in China [35]. Genetic pollution through hybridization is common in Mauremys [14,15,36,37,38,39,40]. A previous study in Japan [30] found a cross-back hybrid between M. japonica and M. reevesii in the wild and reported that the fertility and hatchability of F1 individuals of M. japonica and M. reevesii were not markedly different from those of the parental species, posing a potential threat to the conservation status of M. japonica, which is endemic to mainland Japan. Lee et al. [41] reported that imported M. sinensis has caused genetic hybridization or backcrossing in approximately 57% of protected areas in China, with conservation-critical implications for native M. reevesii populations. As such, human-induced introductions of non-native species are emerging as a significant threat to the conservation of native species. In addition, Fong and Chen [13] also confirmed the occurrence of hybridization between M. sinensis and male M. reevesii in the wild in Taiwan, suggesting the possibility of the genetic integrity of Taiwan’s endemic tortoises being compromised by non-native species. As such, the introduction of non-native species by humans is a serious threat to the conservation of native species.
The most important aspect of establishing a basic management plan for invasive species is to identify the pathways of introduction and regulate the introduction of invasive species [42]. Of the total 2208 alien species introduced to South Korea in 2017, it was reported that about 80% of them could not be identified as to how, why or when they were introduced [43], indicating that the status of imported alien species is not clearly understood. Fortunately, the Ministry of Environment in South Korea has announced the upcoming positive list for imported tetrapods (mammals, birds, amphibians and reptiles) from December 2025. It is believed that this will allow for the management of future invasive species entering the country. However, a management plan for existing invasive species is still required. Therefore, it is necessary to establish an administrative system for the integrated management of invasive reptiles in South Korea, and an integrated organization that can conduct research on invasive species, technology development, removal management and damage assessment should be established. Studies on the management of non-native species in South Korea [1,44,45,46] have primarily focused on policies and legislation that encompass IAS; however, improving laws and policies requires time and financial resources. For rapid and more aggressive conservation, based on the results of the current study, it is recommended that the sympatric area of M. sinensis and M. reevesii should be designated and managed as priority management areas. And the sites inhabited only by M. reevesii (Table 1, No. 29–39) should be protected as habitat and species conservation areas. We suggest that follow-up studies should be carried out on the breeding facilities not included in this study.

5. Conclusions

The study was conducted to identify hybrids between M. Sinensis and M. reevesii at 47 sites throughout the country. A total of seven hybrid individuals were identified in the wild at four sites. At the sites where hybrids were found, two individuals were captured through trapping surveys, and the two individuals collected from captive breeding facilities were genetically analyzed to confirm hybridization. Hybridization may lead to the loss of the unique genotype of the Korean M. reevesii, and to prevent this, more active conservation measures such as nest destruction and capture of individuals using floating traps should be implemented at six sites designated as protected areas. In addition, follow-up studies such as breeding studies and genetic introgression studies should be conducted to ensure the conservation of South Korea’s biodiversity. In addition, more active public outreach and education, such as free collection of abandoned turtles and designation of dumping sites, are needed to prevent the introduction of non-native turtles into the wild.

Author Contributions

Conceptualization, H.-J.B.; data curation, H.-J.B., E.C. and Y.K.; investigation, H.-J.B., K.S.K., S.-H.K., C.-D.P. and J.-D.Y.; software, H.-J.B. and E.C.; visualization Y.K.; writing—original draft, H.-J.B.; writing—review and editing, H.-J.B., E.C., Y.K., K.S.K., S.-H.K., C.-D.P. and J.-D.Y. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by grants from the National Institute of Ecology funded by the Ministry of Environment of Republic of Korea, grant number NIE-A-2024-09.

Institutional Review Board Statement

The animal study protocol was approved by the IACUC at National Institute of Ecology’s Center, South Korea (protocol codes NIEIACUC-2021-027 and NIEIACUC-2022-003 and 31 December 2021 and 31 December 2022).

Informed Consent Statement

Not applicable.

Data Availability Statement

The data presented in this study are openly available in the NIE ECObank repository at https://www.nie-ecobank.kr/rdm/rsrchdoi/selectRsrchDtaDtlVw.do and https://library.me.go.kr/#/search/detail/5841308?offset=10.

Acknowledgments

We would like to thank the members of the Invasive Alien Species Team at the National Institute of Ecology and the students at the Ewha Woman’s University for helping us to carry out the research.

Conflicts of Interest

The authors declare no conflicts of interest. The funders had no role in the design of the study; in the collection, analyses or interpretation of data; in the writing of the manuscript; or in the decision to publish the results.

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Animals 14 02626 g001
Figure 1. Survey sites of Mauremys species in South Korea and species information.
Figure 1. Survey sites of Mauremys species in South Korea and species information.
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Animals 14 02626 g002
Figure 2. External differences among Mauremys sinensis, M. reevesii and their hybrid; (a-1) hybrid found on Jeju Island, (a-2) plastron of hybrid, (b-1) M. sinensis, (b-2) plastron of M. sinensis, (c-1) M. reevesii, and (c-2) plastron of M. reevesii.
Figure 2. External differences among Mauremys sinensis, M. reevesii and their hybrid; (a-1) hybrid found on Jeju Island, (a-2) plastron of hybrid, (b-1) M. sinensis, (b-2) plastron of M. sinensis, (c-1) M. reevesii, and (c-2) plastron of M. reevesii.
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Animals 14 02626 g003
Figure 3. Maximum-likelihood tree based on an analysis of 13 Mauremys individuals using 615 bp of mitochondrial COI sequences, including two Cuora species (C. aurocapitata AY874540 and C. amboinensis NC_014769), with T92 + G and bootstrapping (1000 replications).
Figure 3. Maximum-likelihood tree based on an analysis of 13 Mauremys individuals using 615 bp of mitochondrial COI sequences, including two Cuora species (C. aurocapitata AY874540 and C. amboinensis NC_014769), with T92 + G and bootstrapping (1000 replications).
Animals 14 02626 g003
Animals 14 02626 g004
Figure 4. Maximum-likelihood tree based on an analysis of 13 Mauremys individuals using 863 bp of nuclear R35 sequences, with T92 + I + G and bootstrapping (1000 replications).
Figure 4. Maximum-likelihood tree based on an analysis of 13 Mauremys individuals using 863 bp of nuclear R35 sequences, with T92 + I + G and bootstrapping (1000 replications).
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Table 1. Survey sites of Mauremys species in South Korea, species found, identification methods and individuals used for genetic analysis (M. sinensis/M. reevesii indicates sympatric distribution; M. sinensis × M. reevesii indicates hybridization observed).
Table 1. Survey sites of Mauremys species in South Korea, species found, identification methods and individuals used for genetic analysis (M. sinensis/M. reevesii indicates sympatric distribution; M. sinensis × M. reevesii indicates hybridization observed).
No.LocalitySpeciesIdentification StatusNumber of Individuals ObservedId
1Misa-dong, beon-gil, Hanam-si, Gyeonggi-doM. sinensisobservation1
2Haedoji-ro, Yeonsu-gu, IncheonM. sinensisobservation1
3Haegok-ro, Cheoin-gu, Yongin-si, Gyeonggi-doM. sinensisobservation1
4Anseo-dong, Dongnam-gu, Cheonan-si, Chungcheongnam-doM. sinensisobservation1
5Eumnae-dong, Seosan-si, Chungcheongnam-doM. sinensisobservation1
6Chungjeol-ro, Dongnam-gu, Cheonan-si, Chungcheongnam-doM. sinensisobservation3
7Yongdam-dong, Sangdang-gu, Cheongju-si, Chungcheongbuk-doM. sinensisobservation2
8Mannyeon-dong, Seo-gu, DaejeonM. sinensisobservation2
9Changpo-dong, Buk-gu, Pohang-si, Gyeongsangbuk-doM. sinensisobservation3
10Jangseong-dong, Buk-gu, Pohang-si, Gyeongsangbuk-doM. sinensisobservation1
11Daejam-dong, Nam-gu, Pohang-si, Gyeongsangbuk-doM. sinensisobservation1
12Gyeyang-dong, Gyeongsan-si, Gyeongsangbuk-doM. sinensisobservation2
13Wolgok-ro, Dalseo-gu, DaeguM. sinensisobservation1
14Hwawon-eup, Dalseong-gun, DaeguM. sinensisobservation2
15Naegi-ri, Dongjin-myeon, Buan-gun, Jeollabuk-doM. sinensisobservation1
16Munsu-ro, Nam-gu, UlsanM. sinensisobservation3
17Beomeo-ri, Mulgeum-eup, Yangsan-si, Gyeongsangnam-doM. sinensisobservation1
18Yangsanje-ro, Buk-gu, GwangjuM. sinensisobservation1
19Yongbong-dong, Buk-gu, GwangjuM. sinensisobservation1
20Hwamyeong-dong, Buk-gu, BusanM. sinensisobservation2
21Choeupcheon-dong, Busanjin-gu, BusanM. sinensisobservation8
22Pungam-dong, Seo-gu, GwangjuM. sinensisobservation5
23Beomjeon-dong, Busanjin-gu, BusanM. sinensisobservation3
24UN-ro, Nam-gu, BusanM. sinensisobservation2
25Seodaeshin-dong-ga, Seo-gu, BusanM. sinensisobservation1
26Hadan-dong, Saha-gu, BusanM. sinensisobservation,
DNA analysis		2Tor019, 020
27Samyangil-dong, Jeju-si, Jeju-doM. sinensisobservation1
28Boseong-ri, Daejeong-eup, Seogwipo-si, Jeju-doM. sinensisobservation1
29Gobul-ro, Gwangju-si, Gyeonggi-doM. reevesiiobservation1
30Susan-ri, Geunnam-myeon, Uljin-gun, Gyeongsangbuk-doM. reevesiiobservation1
31Hadae-ri, Gyeryong-myeon, Gongju-si, Chungcheongnam-doM. reevesiiobservation1
32Sinpung-ri, Bujeok-myeon, Nonsan-si, Chungcheongnam-doM. reevesiiobservation3
33Yuhak-ro, Seokjeok-eup, Chilgok-gun, Gyeongsangbuk-doM. reevesiiobservation1
34Hochon-ri, Dasan-myeon, Goryeong-gun, Gyeongsangbuk-doM. reevesiiobservation4
35Cheongun-dong, Gyeongju-si, Gyeongsangbuk-doM. reevesiiobservation1
36Jeongyang-ri, Daeyang-myeon, Hapcheon-gun, Gyeongsangnam-doM. reevesiiobservation2
37Eoseo-ri, Saengcho-myeon, Sancheong-gun, Gyeongsangnam-doM. reevesiiobservation1
38Gurye-eup, Gurye-gun, Jeollanam-doM. reevesiiobservation,
DNA analysis		20Tor411, 412, 413, 414, 415
39Pyeongsa-ri, Agyang-myeon, Hadong-gun, Gyeongsangnam-doM. reevesiiobservation2
40Chimsan-dong, Jung-gu, DaejeonM. sinensis / M. reevesiiobservationM. sinensis: 2
M. reevesii: 12
41Chunggok-ri, Bujeok-myeon, Nonsan-si, Chungcheongnam-doM. sinensis / M. reevesiiobservationM. sinensis: 2
M. reevesii: 1
42Cheonsang-gil, Beomseo-eup, Ulju-gun, UlsanM. sinensis / M. reevesiiobservationM. sinensis: 3
M. reevesii: 3
43Geumsansunhwan-ro, Geumsan-myeon, Jinju-si, Gyeongsangnam-doM. sinensis / M. reevesiiobservationM. sinensis: 5
M. reevesii: 12
44Gwonsamdeuk-ro, Deokjin-gu, Jeonju-si, Jeollabuk-doM. sinensis / M. reevesii
M. sinensis × M. reevesii		observationM. sinensis: 2
M. reevesii: 1
M. sinensis × M. reevesii: 1
45Hak-dong, Yeosu-si, Jeollanam-doM. sinensis × M. reevesiiobservationM. sinensis × M. reevesii: 1
46Gwangnyeong-ro, Aewol-eup, Jeju-si, Jeju-doM. sinensis × M. reevesiiobservation,
DNA analysis		M. sinensis × M. reevesii: 1Tor062
47Namseongjung-ro, Seogwipo-si, Jeju-doM. sinensis × M. reevesiiobservation,
DNA analysis		M. sinensis × M. reevesii: 4Tor274
48In captivity
Hwaseong-si, Gyeonggi-do		M. sinensis × M. reevesii
M. reevesii, M. sinensis		DNA analysisM. reevesii > 20
M. sinensis: 2
M. sinensis × M. reevesii: 2		Tor036, 037
Tor409, 410
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Baek, H.-J.; Cheong, E.; Kim, Y.; Koo, K.S.; Kim, S.-H.; Park, C.-D.; Yoon, J.-D. Geographical Distribution of Mauremys sinensis, Mauremys reevesii, and Their Hybrids in South Korea. Animals 2024, 14, 2626. https://doi.org/10.3390/ani14182626

AMA Style

Baek H-J, Cheong E, Kim Y, Koo KS, Kim S-H, Park C-D, Yoon J-D. Geographical Distribution of Mauremys sinensis, Mauremys reevesii, and Their Hybrids in South Korea. Animals. 2024; 14(18):2626. https://doi.org/10.3390/ani14182626

Chicago/Turabian Style

Baek, Hae-Jun, Eujin Cheong, Youngha Kim, Kyo Soung Koo, Su-Hwan Kim, Chang-Deuk Park, and Ju-Duk Yoon. 2024. "Geographical Distribution of Mauremys sinensis, Mauremys reevesii, and Their Hybrids in South Korea" Animals 14, no. 18: 2626. https://doi.org/10.3390/ani14182626

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