• 제목/요약/키워드: Rana plancyi

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청원군에 소재한 금개구리(Rana plancyi chosenica) 개체군의 번식동태 (Reproductive Dynamics of the Gold-spotted Pond Frog (Rana plancyi chosenica) Population Located at Cheongwon, Korea)

  • 성하철;라남용;정석환;김수경;차상민;박대식
    • 환경생물
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    • 제27권1호
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    • pp.20-30
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    • 2009
  • 환경부지정 멸종위기 II급 종인 금개구리 (Rana plancyi chosenica)의 번식생태를 연구하기 위하여 충북 청원군 장내면에 위치하는 묵논형 습지에 있는 금개구리 개체군을 2007년 4월부터 2008년 11월까지 총 207일에 걸쳐서, 모음담장과 주머니함정을 설치하여 모니터링을 실시하였다. 금개구리들은 봄철 4월 20일부터 6월 13일 사이에 번식지로 이동하였으며, 가을철 동면지 이동은 9월 21일부터 11월 16일 사이에 일어났다. 서식지 내 외로의 이동은 2007년과 가을 이동과 2008년 봄 이동 시 공히 강수와 높은 양의 상관을 보였지만, 기온, 수온, 상대 습도와는 유의미한 상관관계를 보이지 않았다. 금개구리들은 이동 시 주로 논의 언덕이나 묵논과 연결된 이동경로를 다른 경로보다 선호하여 사용하는 것으로 나타났다. 번식지 내 외로의 이동순서와 개체의 신체 요소와는 2007년 봄에는 번식지 내 외로의 이동순서와 개체의 몸길이(snout-vent length)와 양의 상관을 보였으며, 이동순서와 몸무게와는 2008년 봄을 제외한 모든 경우에 양의 상관을 보여, 작은 개체들이 먼저 출현하고 먼저 동면지로 이주하는 경향을 보였다. 금개구리 암컷은 수컷에 비하여 유의미하게 큰 것으로 확인되었으며, 가을철 동면지 이주 시 20mm SVL 크기 이하의 작은 개체들의 수가 2007년, 2008년 공히 소폭 증가하여, 개체군 내에 성공적인 번식이 일어나고 있음을 알 수 있었다. 이러한 연구결과는 금개구리 야외 개체군을 보존하는 기초자료로 활용할 수 있을 것이다.

Detection of Infectious Fungal Diseases of Frogs Inhabiting in Korea

  • Kim, Suk;Eom, Ahn-Heum;Park, Dae-Sik;Ra, Nam-Yong
    • Mycobiology
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    • 제36권1호
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    • pp.10-12
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    • 2008
  • In recent years, there has been a rapid decrease in amphibian populations worldwide, and infectious diseases have been associated with this decline. Diseased frogs inhabiting Korea were collected from fields, and the diseases were identified by morphological and molecular analyses. Two fungal diseases-saprolegniasis and chromomycosis-were detected in the frogs. Saprolegniasis caused by Saprolegnia spp. was found in Rana plancyi chosenica from Gangwon-do and Rana huanrenensis from Chungbuk. Chromomycosis, which is caused by infection with Cladosporium cladosporioides, was detected in Rana catesbeiana from Busan.

Genetic Differentiation among the Mitochondrial ND2 Gene and $tRNA^{Trp}$ Gene Sequences of Genus Rana (Anura) in Korea

  • Lee, Hyuk;Yang, Suh-Yung;Lee, Hei-Yung
    • Animal cells and systems
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    • 제4권1호
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    • pp.31-37
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    • 2000
  • The genetic variations among six species of Rana from Korea (R. nigro-maculata, R. piancyi, R. dybowskii, R. sp, R. rugosa type A, B and R. amurensis) were investigated using 499 bases of mitochondrial DNA sequences for ND2 (NADH dehydrogenase subunit 2) gene and $tRNA^{Trp}$ gene. Partial sequences of ND2 gene (427 bp) and full sequences of $tRNA^{Trp}$ gene (73 bp) were identified. The level of sequence divergences ranged from 0.2 to 5.2% within species and 4.9-28.0% among 6 species of the genus Rana. The $tRNA^{Trp}$ gene of the genus Rana was composed of 77 nucleotides which showed a two dimensional "cloverleaf" structure. The secondary structure of $tRNA^{Trp}$ was not found compensatory changes which could potentially confound phylogenetic inference. In the neighborjoining tree, brown frogs were clustered first with the level of sequence divergence of 13.20% between R. amurensis and R. dybowskii, and 9% between R. dybowskii and R. sp. supported by 99% bootstrap iterations, respectively. R. nigromaculata and R. plancyi were clustered into another group with 5.1% divergence supported by 100% bootstrap iteration. R. rugosa A 8nd B types were grouped by 4.9% divergence and clustered into the last group with other two groups with 100% bootstrap iterations.

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Colonization and Extinction Patterns of a Metapopulation of Gold-spotted Pond Frogs, Rana plancyi chosenica

  • Park, Dae-Sik;Park, Shi-Ryong;Sung, Ha-Cheol
    • Journal of Ecology and Environment
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    • 제32권2호
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    • pp.103-107
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    • 2009
  • We investigated colonization and extinction patterns in a meta population of the gold-spotted pond frog (Rana planeyi ehoseniea) near the Korea National University of Education, Chungbuk, Korea, by surveying the frogs in the nine occupied habitat patches in the study area four times per breeding season for three years (2006$\sim$2008) and recording whether the patches were occupied by frogs as well as how many frogs were calling in the patches. We then developed five a priori year-specific models using the Akaike Information Criterion (AIC). The models predicted that: 1) probabilities of colonization and local extinction of the frogs were better explained by year-dependent models than by constant models, 2) there are high local extinction and low colonization probabilities, 3) approximately 31% number of patches will be occupied at equilibrium, and 4) that considerable variation in occupation rate should occur over a 30-year period, due to demographic stochasticity (in our model, the occupation rate ranged from 0.222 to 0.889). Our results suggest that colonization is important in this metapopulation system, which is governed by mainly stochastic components, and that more constructive conservation effects are needed to increase local colonization rates.

한라산 국립공원의 양서.파충류 현황 및 생물지리학적 고찰 (Current Status and Biogeographical Comments of Herpeto-Fauna at Hallasan National Park)

  • 오홍식;장민호;김병수
    • 한국환경생태학회지
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    • 제21권2호
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    • pp.107-112
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    • 2007
  • 한라산 국립공원의 양서 파충류상을 파악하기 위하여 1100고지, 어승생악, 돈내코, 어리목, 영실, 관음사, 성판악 주변을 2006년 4월부터 2007년 1월까지 조사하였다. 한라산 국립공원에서 발견된 양서류는 총 4과 5종, 파충류는 4과 8종이었다. 내륙 지방에서는 개체수가 적은 대륙유혈목이(Amphiesma vibakari ruthveni), 줄장지뱀(Takydronus wolteri), 도마뱀(Scincella vandenburghi), 실뱀(Coluber spinalis), 제주도룡뇽(Hynobius quelpartensis)과 한반도에서는 제주도에만 서식하는 비바리뱀(Sibynophis chinensis)을 확인하였다. 제주도는 한반도에서 유일하게 남방한계와 북방한계인 양서 파충류가 서식한다. 제주도의 양서 파충류는 오랜 격리와 기후에 의한 차이를 보이며 생물지리학적으로 매우 중요한 위치에 있다. 또한 기존 문헌에 기록되어 있지만, 서식여부가 명확하지 않은 두꺼비(Bufo gargarizans), 옴개구리(Rana rugosa), 금개구리(R. plancyi). 무자치(Elaphe rufodorsata), 아무르장지뱀(T. amurensis)의 현황에 대한 연구는 시급히 이루어져야 한다.

도시 산림습지 내 양서류 서식처 조성방안 연구 (Planning for Amphibians Habitats in Urban Forest Wetlands, Korea)

  • 허명진;한봉호;곽정인
    • 한국환경복원기술학회지
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    • 제20권6호
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    • pp.1-19
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    • 2017
  • This study set out to identify problems with amphibian habitation by the wetland types and improve their habitation environment in urban forest wetlands, thus creating a habitat for amphibians. Study site include forest swamps in Jatjul Park as well as Yeoji neighborhood Park in Guro-gu, and in Choansan neighborhood Park in Dobong-gu. The forest swamp in Jatjul Park gets its water from Mt. Maebong and it is a former escalated farmland-turned wetland. The swamp area is $2,500m^2$, a forest zone and a landscape planting site are 83.27% and 6.70% each. Target species Seoul pond frogs are inseparable from rice fields because they live in a short radius of and lay eggs in or near paddy fields, and Rana nigromaculata have similarities with Rana plancyi chosenica in choosing their habitats. There was need for paths that would lead to other paths so amphibians would spread to other parts of the forest and for measures to secure open water. Modifying a variety of routes for water, human and animals along with building a buffer to keep the core habitation zones were required. The forest swamp in Yeonji neighborhood Park used to be a water reservoir on the foot of Mt. Gunji. The swamp area is $1,980m^2$, a forest zone and farmland account for 80.61% and 4.88% each. Non-point pollutants from upstream along run into the subject forest marsh, bare ground on the around swamp and steep stone embankments obstructed amphibians. Target species was Bufo gargarizans that live in forests and edges of hills and spawn in deep water. The forest swamp in Choansan neighborhood Park gets its water from Mt. Choan and it is close to its water source that it is a mountain stream forest wetland. The basin and the swamp are $35,240m^2$ and $250m^2$ in size respectively. A forest zone accounts for 90.20%, high stone embankments laid in refurbishing the valley obstruct amphibians and there is water shortage in times of droughts. Target species were Rana coreana, Rana dybowskii and Hynobius leechii that live in mountain valleys, streams and wetlands and lay eggs in forest marshes and rocks in valleys. Looking into the three swamps of amphibian habitation, I came to conclusions that those wetlands were suitable for their amphibians but man-made facilities blocked their corridors leading to other corridors and even killed off target species in some parts of those swamps by destroying those parts. Amphibians live in water, on ground and underground at different stages of life. Hence, we should take this fact into consideration when planning their habitats and design core habitation zones, buffers zone and use zones accordingly. Buffer zones ought to be between core habitation zones and surrounding trees. Aiming at protecting core habitation zones, buffers should be in harmony with habitation zones. Use zones should be minimized in size and not in direct contact with core habitation zones.

시스템 사고를 통한 다기능 생태저류지의 관리방안 - 광명 안터생태공원을 중심으로 - (The Management Methods of Multi-Purpose Ecological Reservoir by System Thinking - Focused on Anteo Eco Park -)

  • 이현지;유수진;전진형
    • 한국환경복원기술학회지
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    • 제18권2호
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    • pp.1-17
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    • 2015
  • Ecological reservoir is a multifunctional space where provides the functions of retention, animal habitat and improvement of ecosystem health and landscape. The ecological reservoir of Anteo Eco Park located in Gwangmyeong-si has established to functions for water purification, maintenance of healthy aquatic ecosystem. Because the Anteo Eco Park is located in the site where nonpoint pollutant materials flow in, Anteo Eco Park has potential factors which aquatic ecosystem health deteriorates and damages the habitat of golden frog(Rana plancyi chosenica) which is restoration target species. Therefore, the purpose of this study is to suggest the plan to manage the variables which impede the right functions of aquatic ecosystem by understanding the causal loop diagram for the change of water quality environment and the interaction of predator-prey through system thinking. The results are as follows. First, the study showed that the individual number of golden frog which is an indicator species of Anteo Eco Park is threatened by snakeheaded fish, which is an upper predator. Therefore, balanced food chain should be hold to protect golden frog by capturing the snakeheaded fish which is individual number's density is high, and the monitoring management of the individual number for predator(snakeheaded fish)-prey(golden frog) should be performed. Second, the study represented that water pollution and carnification is caused by the sediment as the dead body of the large emergent vegetation in the winter cumulates as sediment. Ecological reservoir in Anteo Eco Park has been managed by eliminating the dead body of the large emergent vegetation, but the guideline for the proper density maintenance of vegetation community is additionally needed. Lastly, the study showed that aquatic ecosystem of Anteo Eco Park where is contaminated from the inflow of nonpoint pollutants affects the individual number's decline of golden frog and snakeheaded fish. Accordingly, the creation of a buffer area and a substitution wetland is needed in the periphery of the Anteo Eco Park to control the inflow of nonpoint pollutants including organic matters, nutrients and heavy metals. This study will be helpful that Anteo Eco Park improves the regional landscape and maintain healthy aquatic ecosystem space for the park visitors including local residents.