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ISSN : 1226-9999(Print)
ISSN : 2287-7851(Online)
Korean J. Environ. Biol. Vol.43 No.1 pp.1-9
DOI : https://doi.org/10.11626/KJEB.2025.43.1.001

Population size and structure of endangered Reeves’ turtle (Mauremys reevesii ) in Geumho Reservoir, the Republic of Korea: Possibility of the largest population

Hakyung Kang1, Jeong Min Oh1, Yikweon Jang2, Kyo Soung Koo3,4,*
1Division of EcoScience, Ewha Womans University, Seoul 03760, Republic of Korea
2Department of Life Sciences, Ewha Womans University, Seoul 03760, Republic of Korea
3Research Institute of EcoScience, Ewha Womans University, Seoul 03760, Republic of Korea
4Korean Environmental Geography Institute, Sejong 30141, Republic of Korea
*Corresponding author Kyo Soung Koo Tel. 044-589-3454 E-mail. flqpfj@hanmail.net

Contribution to Environmental Biology


▪ In this study, we identified the largest known population of the endangered Reeves’ turtle (Mauremys reevesii ) in Geumho Reservoir, the Republic of Korea.


▪ Our findings highlight an urgent need for immediate conservation measures and provide compelling justification for designating Geumho Reservoir as a specially protected area.


29/10/2024 21/11/2024 02/12/2024

Abstract


Mauremys reevesii (Reeves’ turtle) is an endemic freshwater turtle species found throughout East Asia. Due to a rapid population decline, the International Union for Conservation of Nature (IUCN) and the Korean government have classified this species as Endangered (EN). The reported largest population size of M. reevesii in the Republic of Korea was previously estimated to be approximately 20-30 individuals. Our study assessed the population size and structure of M. reevesii at Geumho Reservoir, Republic of Korea, using a capture-recapture data. A total of 433 M. reevesii were incidentally captured during a 35-week trapping process conducted from March to October 2023. The sex ratio of the captured population exhibited a male bias of 1.3 : 1. Sexual size dimorphism was observed only in body weight. Individuals were recaptured up to 11 times during the study period, with males and females being recaptured at an average of 2.1±2.0 times and 1.5±0.9 times, respectively. The estimated population size of M. reevesii in Geumho Reservoir was approximately 891 turtles. The absence of notable sexual size dimorphism and significant sex ratio differences suggests that the population in this area may have been established relatively recently. Compared to previous records, the population in Geumho Reservoir represents the largest single population of M. reevesii, both within the Republic of Korea and globally.



초록


    1. INTRODUCTION

    Mauremys reevesii (Reeves’ turtle), a member of the family Geoemydidae, has a geographic range that extends across Asia, including the Korean Peninsula, China, Taiwan, and Japan (GBIF 2023). This turtle was once commonly found in reservoirs, rivers, and lakes. However, its population is rapidly declining due to habitat destruction, overharvesting, and genetic pollution resulting from hybridization with other species (Lee 2010;Lovich et al. 2011;Baek et al. 2024). Moreover, the shell of M. reevesii, which contains musk, was historically used as a high-grade medicinal ingredient. Recently, its popularity as a pet has made it a target for poaching (Cheung and Dudgeon 2006;Chen et al. 2009). As a result, the International Union for Conservation of Nature (IUCN) Red List has assessed the status of M. reevesii as Endangered (EN) (Van Dijk 2011). In the Republic of Korea, M. reevesii has been designated as Natural Monument No. 453 and classified as an Endangered Wildlife Species Class II, ensuring its conservation through government management (NIBR 2011).

    The known population sizes of M. reevesii have generally not exceeded 30 individuals per site, with two notable exceptions: 1,123 individuals recorded across Ishima Island, Japan (Takenaka and Hasegawa 2001), and 110 individuals documented by Yabe (1994) over a two-year period (Chen and Lue 2010;Lovich et al. 2011;Bu et al. 2022a). In the Republic of Korea, the number of turtles found in each location is typically less than 10 individuals (Lee 2010). Recently, the largest population of this species in the Republic of Korea was discovered in a small reservoir in Gyeongju-si, comprising approximately 20-30 individuals (Koo et al. 2019). Moreover, M. reevesii are highly elusive, making them difficult to detect during standard visual surveys. This characteristic poses challenges in accurately estimating their population size (Lovich et al. 2011;Kim et al. 2013).

    In this study, we examined the population size and structure of M. reevesii in Geumho Reservoir, Jinjusi, the Republic of Korea. Our findings confirm the potential of Geumho Reservoir as a significant habitat for the largest known population of this endangered turtle species.

    2. MATERIALS AND METHODS

    The research on the development of capture techniques for invasive turtles, conducted by Ewha Womans University under the supervision of the Korea Environmental Industry & Technology Institute (KEITI), an affiliate of the Ministry of Environment, was carried out from 2021 to 2023 (KEITI 2024). Our study was conducted from March to October 2023.

    2.1. Study area

    The research area is Geumho Reservoir located in Geumsan-myeon, Jinju-si, Gyeongsangnam-do (35°12ʹ 29ʺN, 128°9ʹ13ʺE, WGS 84, 37 m a.s.l.), with an area of approximately 20 ha. This reservoir serves multiple purposes, including supplying agricultural water and providing recreational opportunities for local citizens. Recent studies have documented the presence of various turtle species in the reservoir, including the native M. reevesii and the invasive red-eared slider (Trachemys scripta elegans) (Yun et al. 2022).

    2.2. Sampling target species

    In this study, we utilized M. reevesii specimens that were collected during research on developing capture techniques for invasive turtles, rather than directly capturing them for this study (Kim et al. 2020). Within the reservoir, we selected two locations where numerous individuals were observed during visual surveys for invasive turtles (Fig. 1). At these sites, three types of capture devices (centipede net type, floating type, and falling type) developed by Ewha Womans University were installed (Appendix Fig. A1). The centipede net traps (45×30 cm, length 7-10 m) were installed around aquatic plants to capture individuals moving at the water surface and between aquatic plants near the shoreline. The floating traps (60×60×25 cm) are designed to be installed on open water surfaces with depth to capture basking and submerged individuals (patent number: 10-2507736). The falling traps (90×90×40 cm) are placed under natural structures like submerged trees to capture basking individuals. A total of 17 traps were installed, including 3 centipede net traps, 13 floating traps, and 1 falling trap, to capture turtles. From March 16 to October 31, 2023, we conducted weekly visits to the reservoir, totaling 35 weeks. During each visit, we recorded the species and size of turtles captured in each trap. The captured invasive turtles were collected, while M. reevesii were released back into the water. The installation of turtle traps and capture activities in this study were permitted by Jinju local government (official document: Environmental Management Division-39161), and Han River Basin Environmental Office (2022-02).

    2.3. Population structure

    The straight carapace length (SCL) of turtles was measured using a vernier caliper (Mitutoyo, Japan), and their body weight (BW) was measured using an electronic scale (WK-4CII, CAS, China). When determining the sex of freshwater turtles in the field, it is typically noted that males have longer tails than females (Lin et al. 2017;Yadollahvandmiandoab et al. 2018). Individuals were identified as males when the cloaca extended more than 2 cm beyond the edge of the carapace and had a long tail. Females were identified when the cloaca was close to the edge of the carapace. Smaller individuals whose sex could not be determined were recorded as juveniles (Rodrigues et al. 2014;Oh et al. 2015).

    For individual marking, methods such as inserting small electronic chips (PIT tagging), attaching transmitters, or marking identification numbers by drilling holes in the marginal scutes of the carapace are used (Cagle 1939;Obbard and Brooks 1981;Gibbons and Andrews 2004;Nagle et al. 2017). In contrast, non-invasive methods include using the individual’s unique patterns or utilizing eco-friendly paint markers (Rowe et al. 2012;Unger and Santana 2019). In this study, we employed a non-invasive method based on Cagle’s proposed technique, using non-toxic paint markers (Permanent Marker, LYRA, Germany) to minimize the impact on the individuals. Numbers were assigned to the marginal scutes on the rear part of the carapace, and each individual’s identification number was marked on these scutes (Fig. 2).

    2.4. Sexual size dimorphism and analysis

    Freshwater turtles typically exhibit distinct sexual dimorphism (Berry and Shine 1980;Lovich and Gibbons 1990). To understand the population structure in Geumho Reservoir, we analyzed the sex ratio based on the number of individuals captured. Sexual size dimorphism was analyzed by comparing the SCL and BW of females and males using independent samples t-tests. Differences in recapture frequency between sexes were analyzed using a chi-square test, while the number of recaptures between sexes was compared using an independent samples t-test. All statistical analyses were performed using SPSS Statistics version 23.0 (IBM, USA).

    2.5. Population size estimation

    To estimate the population size of M. reevesii in Geumho Reservoir, we employed the Schnabel method, which uses capture-recapture data to estimate potential population size (Schnabel 1938). The estimation formula is as follows:

    N = ( Σ C t M t ) / ( Σ R t )
    (1)

    N: Estimated population size; Ct: Total number of individuals caught at time t; Mt: Number of marked individuals before sampling at time t; Rt: Number of recaptured animals at time t.

    3. RESULTS

    3.1. Population structure

    During the study period, we identified a total of 433 turtles, comprising 180 females, 235 males, and 18 juveniles (Fig. 3). The overall sex ratio of females to males was 1 : 1.3. Female turtles (n=180) had a mean SCL of 98.7±27.5 mm (range: 59.8-199.3 mm) and a mean BW of 179.0±167.3 g (range: 37.0-1,133.0 g). Male turtles (n=235) had a mean SCL of 97.2±24.4 mm (range: 58.3-167.9 mm) and a mean BW of 150.8±102.5 g (range: 35.0-515.0 g). Juveniles (n=18) measured 52.4±6.1 mm (range=34.8-59.4 mm) in SCL and 26.8±8.0 g (range=7.0-39.0 g) in BW. There was no significant difference in SCL between females and males (independent samples t-test, t=0.552, df=415, p= 0.581). However, females were significantly heavier than males in BW (t=2.119, df=415, p=0.047).

    3.2. Rate of recapture

    During the study period, M. reevesii were recaptured a total of 191 times. Among these recaptures, 65 individuals (15.0%) were recaptured only once (Fig. 4). The recapture frequency decreased significantly to less than half for the second recapture (n=13) and further declined for the fourth recapture (n=3). The recapture rate by sex was higher for males at 28.9% (n=68/235) compared to females at 17.2% (n=31/180) (chi-square test, χ2=13.828, df=1, p<0.0001). The average number of recaptures was also higher for males, at 2.1±2.0 times (range: 1 to 11), compared to females at 1.5±0.9 times (range: 1 to 4). However, this difference was not statistically significant (t=1.962, df=96.883, p=0.053).

    3.3. Population size estimation

    Based on the capture-recapture results over a total of 35 weeks, the population size of M. reevesii inhabiting Geumho Reservoir was estimated to be approximately 891.4 individuals.

    4. DISCUSSION

    Our study showed that the Geumho Reservoir is a habitat for the largest population of M. reevesii in the Republic of Korea. During the study period, at least 433 individuals were identified, which is more than 20 times the previous record for the largest population of this species in the Republic of Korea (Koo et al. 2019). Moreover, compared to international cases, except for the record of 1,123 individuals by Takenaka and Hasegawa (2001) (with the number of individuals per site unknown), the population in Geumho Reservoir is several to several dozen times larger (Yabe 1994;Suzuki et al. 2011;Bu et al. 2022a). Since the capture traps were not set up to cover the entire area of Geumho Reservoir, it is estimated that the actual number of individuals is likely to be much higher. In other words, Geumho Reservoir may be the largest habitat for M. reevesii not only in the Republic of Korea but also globally as a single site. Although further research is needed, these results indicate that Geumho Reservoir, a habitat for the globally endangered M. reevesii, should be designated as a specially protected area and managed at the national level.

    The recapture rate is a crucial variable for estimating population size (Schnabel 1938;Jolly 1965;Seber 1965;Begon 1979). In the case of turtles, the recapture rate typically does not exceed 30%, even in long-term studies (Jones and Hartfield 1995;Koch et al. 2007). For example, in the case of the wood turtle (Glyptemys insculpta) inhabiting Pennsylvania, the average recapture rate per individual was less than three over a research period of more than 24 years (Lovich et al. 1990). In contrast, this study recorded a recapture rate close to 44% over approximately eight months, with one individual being recaptured 11 times, which accounts for about 30% of the total 35 capture trials. The core home range of M. reevesii averages 2.9 ha, which is narrower than that of the red-eared sliders (2.8-7.6 ha) and its close relative, Iberian pond turtle, Mauremys leprosa (2.2-4.07 ha) (Pérez-Santigosa et al. 2013;Song et al. 2014;Bu et al. 2023). It is likely that M. reevesii has a narrow home range and therefore did not stray far from their habitat after release, which may have contributed to the high recapture rate. While further research on habitat preference is needed, if this hypothesis is correct, these characteristics may render them highly vulnerable to illegal poaching and habitat disturbance.

    There was no clear sexual size dimorphism observed between the sizes of females and males inhabiting Geumho Reservoir. Typically, turtles exhibit female-biased sexual size dimorphism, a phenomenon that is also pronounced in M. reevesii (Berry and Shine 1980;Yabe 1994;Noda and Kamata 2004;Lovich et al. 2011;Bu et al. 2022a). In contrast, we found that sexual dimorphism in SCL was not pronounced between females and males. Furthermore, the average SCL of M. reevesii in Geumho Reservoir, measuring 98.7 mm, was significantly smaller than the average SCL of 138.2 mm recorded for females in the Republic of Korea and also showed substantial differences from sizes reported in previous studies (Yabe 1994;Noda and Kamata 2004;Bu et al. 2022b). In the Republic of Korea, prior to the importation of red-eared sliders in the 2000s, M. reevesii was imported from China and released into rivers and reservoirs nationwide (Oh and Hong 2007). It is plausible that the population in Geumho Reservoir was established by turtles introduced during this period. While M. reevesii endemic to the Republic of Korea do not differ taxonomically from the imported Chinese turtles, they possess a unique haplotype specific to the Republic of Korea (Oh et al. 2017). In other words, if the M. reevesii are from China, hybridization with native individuals may occur, potentially leading to a long-term reduction in the unique genetic makeup of the Korean population. Therefore, to protect the unique genetic material of M. reevesii of the Republic of Korea, it is necessary to conduct phylogenetic studies on the turtles in Geumho Reservoir to determine their origin.

    The sex ratio of M. reevesii is reported to be 1 : 1 in individuals under six years old; however, it is generally observed that the proportion of males increases with age (Lovich et al. 2011). In Japan, on Ishima Island, the ratio of males to females has been found to reach as high as 4 : 1 (Takenaka and Hasegawa 2001;Lovich et al. 2011). Several factors have been identified as contributing to the male-biased ratio, with growth rates and female mortality rates being the primary ones (Gibbons 1990). Additionally, roadkill resulting from the high mobility of females also affects the sex ratio (Aresco 2005). The sex ratio of M. reevesii confirmed in our study was slightly male-biased at 1.3 : 1. Based on previous cases, this may support the notion that the population in Geumho Reservoir is not a well-established group over a sufficiently long period. Since the proportion of males does not always increase over time, longterm research is necessary to accurately describe the population structure.

    5. CONCLUSION

    Although this study was conducted on the turtles that were incidentally captured, it provided valuable insights into the population size of this endangered species. In particular, we confirmed the possibility on the largest population of M. reevesii not previously observed in any other country, including the Republic of Korea. M. reevesii is a freshwater turtle that is rapidly declining not only in the Republic of Korea but also globally. Therefore, it is crucial to swiftly develop and implement comprehensive protection measures for this species. Moreover, management strategies for Geumho Reservoir should be established to preserve the habitats and populations of this endangered species, which holds significant importance both nationally and globally.

    ACKNOWLEDGEMENTS

    We would like to thank the lab members of Ewha Womans University for their assistance in the field survey. This research was supported by the Korea Environmental Industry & Technology Institute (KEITI) (grant number: RS-2021-KE001362) and the Basic Science Research Program through the National Research Foundation of Korea (NRF) funded by the Ministry of Education (grant number: RS-2024-00413107).

    CRediT authorship contribution statement

    H Kang: Data curation, Investigation, Writing-Original draft preparation. JM Oh: Data curation, Investigation, Writing-Reviewing and editing. Y Jang: Resources, Writing-Reviewing and editing. KS Koo: Conceptualization, Methodology, Formal analysis, Writing-Original draft preparation, Supervision, Writing-Reviewing and editing.

    Declaration of Competing Interest

    The authors declare no conflicts of interest.

    Figure

    KJEB-43-1-1_F1.gif

    Geumho Reservoir located in Jinju -si, Gyeongsangnamdo, the Republic of Korea. Yellow rectangles indicate locations where traps were set to capture invasive turtles.

    KJEB-43-1-1_A1.gif

    Types of traps used for collecting turtles. (A) A centipede net trap, (B) a floating trap, (C) a falling trap.

    KJEB-43-1-1_F2.gif

    Method for assigning and marking identification numbers to individual Mauremys reevesii. (A) Numbers for each marginal scute of the carapace, (B) number combination method (e.g., 284).

    KJEB-43-1-1_F3.gif

    Distribution of the straight carapace length (SCL) in the Mauremys reevesii population in Jinju -si, the Republic of Korea.

    KJEB-43-1-1_F4.gif

    Number of recaptures for male and female Mauremys reevesii in this study.

    Table

    Reference

    1. Aresco MJ. 2005. The effect of sex-specific terrestrial movements and roads on the sex ratio of freshwater turtles. Biol. Conserv. 123:37-44.
    2. Baek HJ, E Cheong, Y Kim, KS Koo, SH Kim, CD Park and JD Yoon. 2024. Geographical distribution of Mauremys sinensis, Mauremys reevesii, and their hybrids in South Korea. Animals 14:2626.
    3. Begon M. 1979. Investigating Animal Abundance: Capture - Recapture for Biologists. Edward Arnold Ltd. London, UK. p. 97.
    4. Berry JF and R Shine. 1980. Sexual size dimorphism and sexual selection in turtles (Order Testudines). Oecologia 44:185-191.
    5. Bu R, Z Ye and HT Shi. 2022b. Hibernation in Reeves’ turtles (Mauremys reevesii ) in Qichun County, Hubei Province, China: Hibernation beginning and end and habitat selection. Animals 12:2411.
    6. Bu R, Z Ye and HT Shi. 2023. Habitat selection and home range of Reeves’ turtle (Mauremys reevesii ) in Qichun County, Hubei Province, China. Animals 13:1514.
    7. Bu R, Z Ye, F Xiao and HT Shi. 2022a. A survey of Reeves’ turtle (Mauremys reevesii ) in Qichun County, Hubei Province, China. Chelonian Conserv. Biol. 21:212-217.
    8. Cagle FR. 1939. A system of marking turtles for future identification. Copeia 1939:170-173.
    9. Chen TH and KY Lue. 2010. Population status and distribution of freshwater turtles in Taiwan. Oryx 44:261-266.
    10. Chen TH, HC Chang and KY Lue. 2009. Unregulated trade in turtle shells for Chinese traditional medicine in East and Southeast Asia: The case of Taiwan. Chelonian Conserv. Biol. 8:11-18.
    11. Cheung SM and D Dudgeon. 2006. Quantifying the Asian turtle crisis: Market surveys in southern China, 2000-2003. Aquat. Conserv.-Mar. Freshw. Ecosyst. 16:751-770.
    12. GBIF. 2023. Species Mauremys reevesii. Dataset. Global Bio-diversity Information Facility. https://www.gbif.org/species/2443597. Accessed September 12, 2024.
    13. Gibbons JW. 1990. Sex ratios and their significance among turtle populations. pp. 171-182. In: Life History and Ecology of the Slider Turtle. Smithsonian Institute Press. Washington, D. C., USA.
    14. Gibbons WJ and KM Andrews. 2004. PIT tagging: Simple technology at its best. Bioscience 54:447-454.
    15. Jolly GM. 1965. Explicit estimates from capture-recapture data with both death and immigration-stochastic model. Biometrika 52:225-247.
    16. Jones RL and PD Hartfield. 1995. Population size and growth in the turtle Graptemys oculifera. J. Herpetol. 29:426-436.
    17. KEITI. 2024. Development of a Technology to Reduce the Popu-lation of Alien Amphibians and Reptiles using Behavioral Ecology (2nd stage). Report No. TRKO202400012042. Korea Environmental Industry & Technology Institute, Ministry of Environment. Seoul, South Korea. p. 207.
    18. Kim HJ, KS Koo, S Kwon, AJ Kim, H Kang, JY Seo and Y Jang. 2020. Efficiency of invasive turtle trap using behavioral ecology. p. 80. In: Proceedings of the 2020 General Meeting and Conference of Korean Society of Environment and Ecology. Korean Society of Environment and Ecology. Seoul, South Korea.
    19. Kim SR, JH Lee, JY Song, MH Chang, HC Sung and DG Cho. 2013. A study on the habitat restoration model for Chinemys reevesii. J. Korean Soc. Environ. Restor. Technol. 16:115-125.
    20. Koch V, LB Brooks and WJ Nichols. 2007. Population ecology of the green/black turtle (Chelonia mydas) in Bahía Magdalena, Mexico. Mar. Biol. 153:35-46.
    21. Koo KS, HJ Jang, DI Kim, SH Kim, HJ Baek and HC Sung. 2019. Report on the large population and habitat status of endangered species, Mauremys reevesii Gray 1831 (Reptilia; Testudines; Geoemydidae) in South Korea. Korean J. Environ. Ecol. 33:402-407.
    22. Lee HJ. 2010. Distribution and characteristics of Reeve’s turtle (Chinemys reevesii ) populations in Jeolla -do and Gyeong-sangnam-do. M.S. thesis. Kangwon National University. Chuncheon, Korea.
    23. Lin L, D Gaillard, Q Hu, J Yang, Z Chen, F Zhou and HT Shi. 2017. Sexual dimorphism in body size and shape of Beal’s eyed turtle (Sacalia bealei ). Chelonian Conserv. Biol. 16:180-184.
    24. Lovich JE and JW Gibbons. 1990. Age at maturity influences adult sex ratio in the turtle Malaclemys terrapin. Oikos 59:126-134.
    25. Lovich JE, CH Ernst and JF McBreen. 1990. Growth, maturity, and sexual dimorphism in the wood turtle, Clemmys insculpta. Can. J. Zool. 68:672-677.
    26. Lovich JE, Y Yasukawa and H Ota. 2011.Mauremys reevesii (Gray 1831) Reeves’ turtle, Chinese three-keeled pond turtle. pp. 050.051-050.010. In: Conservation Biology of Freshwater Turtles and Tortoises: A Compilation Project of the IUCN/SSC Tortoise and Freshwater Turtle Specialist Group (Rhodin AGJ, PCH Pritchard, PP van Dijk, RA Saumure, KA Buhlmann, JB Iverson and RA Mittermeier, eds.). Chelonian Research Monographs No. 5. Chelonian Research Foundation.
    27. Nagle RD, OM Kinney, JW Gibbons and JD Congdon. 2017. A simple and reliable system for marking hard-shelled turtles: the North American code. Herpetol. Rev. 48:327-330.
    28. NIBR. 2011. Red Data Book of Endangered Amphibians and Rep-tiles in Korea. National Institute of Biological Resources. Incheon, Korea. p. 125.
    29. Noda H and N Kamata. 2004. Relationships between population traits and food habits in aquatic turtles. Bull. Herpetol. Soc. Jpn. 2004:123-133.
    30. Obbard ME and RJ Brooks. 1981. A radio-telemetry and mark-recapture study of activity in the common snapping turtle, Chelydra serpentina. Copeia 1981:630-637.
    31. Oh BK, JH Kang, SH Nam, YJ Lee, SK Lee, BR Hyun, HY Yang and JD Lim. 2015. Classification of native, introduced, and hybrid Reeve’s turtle (Mauremys reevesii ) by morphological characteristics. pp. 31-32. In: Proceedings of the 2015 Annual Meeting and Conference of Korean Society of Environment and Ecology. Korean Society of Environment and Ecology. Goyang, Korea.
    32. Oh HS and CE Hong. 2007. Current conditions of habitat for Rana catesbeiana and Trachemys scripta elegans imported to Jeju-do, including proposed management plans. Korean J. Environ. Ecol. 21:311-317.
    33. Oh HS, SM Park and SH Han. 2017. Mitochondrial haplotype distribution and phylogenetic relationship of an endangered species Reeve’s turtle (Mauremys reevesii ) in East Asia. J. Asia -Pac. Biodivers. 10:27-31.
    34. Pérez-Santigosa N, J Hidalgo-Vila and C Díaz-Paniagua. 2013. Comparing activity patterns and aquatic home range areas among exotic and native turtles in southern Spain. Chelonian Conserv. Biol. 12:313-319.
    35. Rodrigues J, D Soares and J Silva. 2014. Sexing freshwater turtles: Penile eversion in Phrynops tuberosus (Testudines: Chelidae). Acta Herpetol. 9:259-263.
    36. Rowe JW, JR Gradel, CF Bunce and DL Clark. 2012. Sexual dimorphism in size and shell shape, and dichromatism of spotted turtles (Clemmys guttata ) in Southwestern Michigan. Amphib. Reptil. 33:443-450.
    37. Schnabel ZE. 1938. The estimation of the total fish population of a lake. Am. Math. Mon. 45:348-352.
    38. Seber GAF. 1965. A note on the multiple-recapture census. Biometrika 52:249-260.
    39. Song JY, MH Chang and KS Koo. 2014. Distribution and movement of Reeve’s turtle (Mauremys reevesii ) in South Korea. Chin. J. Wildl. 35:239-334.
    40. Suzuki D, H Ota, HS Oh and T Hikida. 2011. Origin of Japanese populations of Reeves’ pond turtle, Mauremys reevesii (Reptilia: Geoemydidae), as inferred by a molecular approach. Chelonian Conserv. Biol. 10:237-249.
    41. Takenaka T and M Hasegawa. 2001. Female-biased mortality and its consequence on adult sex ratio in the freshwater turtle Chinemys reevesii on an island. Curr. Herpetol. 20:11-17.
    42. Unger SD and A Santana. 2019. Turtles and trail cameras: Non-invasive monitoring using artificial platforms. Basic Appl. Herpetol. 33:93-100.
    43. Van Dijk PP. 2011.Mauremys reevesii (errata version published in 2016). The IUCN Red List of Threatened Species 2011: e.T170502A97431862.
    44. Yabe T. 1994. Population structure and male melanism in the Reeves’ turtle, Chinemys reevesii. Jpn. J. Herpetol. 15:131- 137.
    45. Yadollahvandmiandoab R, DO Santana, N Bashirichelkasari and DO Mesquita. 2018. Sexual dimorphism in the Caspian pond turtle, Mauremys caspica. Herpetol. Notes 11:307-309.
    46. Yun K, J Oh, K Koo and Y Jang. 2022. Characteristic analysis of invasive turtles inhabiting Jinju Geumho reservoir according to period and habitation environment. p. 214. In: Proceedings of the 2022 Annual Meeting and International Conference of the Korean Society of Environmental Biology. Korean Society of Environmental Biology. Busan, Korea.

    Vol. 40 No. 4 (2022.12)

    Journal Abbreviation 'Korean J. Environ. Biol.'
    Frequency quarterly
    Doi Prefix 10.11626/KJEB.
    Year of Launching 1983
    Publisher Korean Society of Environmental Biology
    Indexed/Tracked/Covered By

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