棘胸蛙种群分布和景观生态稳定性相关性研究
|
摘要
为研究棘胸蛙野生种群分布与景观生态稳定性的关系,2017年9月至2018年9月,采用样带、样方法对炎陵县境内不同生境中的棘胸蛙野生种群数量进行调查,结合湖南省"十三五"森林资源规划设计调查数据,应用稳定性评价模型对炎陵县景观生态格局稳定性进行分析,并与棘胸蛙野生种群分布进行相关性分析。结果表明:棘胸蛙野生种群数量较少,为82811只±26279只,主要分布于炎陵县东部景观生态稳定性较好的天然阔叶林生境中;景观生态稳定性较差且生境破碎化严重的区域分布较少甚至没有。
In order to understand the population distribution of Paa spinosa in Zhuzhou Yanling County,and the relationship between population and ecological environment,and scientific protection of wild resources of the frog. We investigated the population size of Q. spinosa in different habitats using transect and sample methods,The stability of ecological landscape pattern in Yanling mountain area was analyzed by using"13 th Five-Year"planning and design of forest resources survey data and The stability evaluation model,Kriging interpolation method and boxplot method from September 2017 to September 2018. The results show that the frog mainly located in the eastern part of Yanling where the landscape ecological stability is better,and habitat is natural broad-leaved forest habitat area,But the population is small. The population of Q. spinosa in Yanling mountain area is 82811±26279. It is suggested to strengthen the protection of Q. spinosa wild resources.
In order to understand the population distribution of Paa spinosa in Zhuzhou Yanling County,and the relationship between population and ecological environment,and scientific protection of wild resources of the frog. We investigated the population size of Q. spinosa in different habitats using transect and sample methods,The stability of ecological landscape pattern in Yanling mountain area was analyzed by using"13 th Five-Year"planning and design of forest resources survey data and The stability evaluation model,Kriging interpolation method and boxplot method from September 2017 to September 2018. The results show that the frog mainly located in the eastern part of Yanling where the landscape ecological stability is better,and habitat is natural broad-leaved forest habitat area,But the population is small. The population of Q. spinosa in Yanling mountain area is 82811±26279. It is suggested to strengthen the protection of Q. spinosa wild resources.
引文
[1]陈冬洋.基于MCR和稳定性模型的东方市景观格局空间优化研究[D].长沙:中南林业科技大学.2016.
[2]董雅雯,佘济云,陈冬洋,等.基于箱线图的海南省东方市景观生态格局稳定性研究[J].中南林业科技大学学报,2016,36(8):104-108.
[3]费梁,胡淑琴.中国动物志两栖纲(中卷)无尾目[M].北京:科学出版社.2009.
[4]江建平,谢锋,臧春鑫,等.中国两栖动物受威胁现状评估[J].生物多样性,2016,24(5):588-597.
[5]廖常乐,王合升,黄娟,等.鹦哥岭自然保护区鹦哥岭树蛙种群分布及数量调查[J].动物学杂志,2013,48(3):377-381.
[6]潘晓赋,周伟,周用武,等.中国两栖类种群生态研究概述[J].动物学研究,2002,23(5):426-436.
[7]汪松,解焱.中国物种红色名录(第1卷红色名录)[M].北京:高等教育出版社.2004.
[8]王希臣,付梅臣,刘宗强,等.土地利用规划中建设用地需求量预测的两种模型比较—以东方市为例[J].资源与产业,2009,11(5):87-91.
[9]杨伟国.人工驯养棘胸蛙的繁殖研究[J].动物学杂志,1992,27(3):14-16.
[10]俞宝根.棘胸蛙不同地区的两性异形及人工环境下繁殖行为研究[D].杭州:浙江师范大学,2010.
[11]虞鹏程.赣东北棘胸蛙蝌蚪栖息地生物因子研究[J].四川动物,2000,19(3):163-164.
[12]杨保国.棘胸蛙的生态习性与人工养殖方法[J].生物学杂志,1990,(4):19-23.
[13]赵尔宓.中国濒危动物红皮书——两栖类和爬行类[M].北京:科学出版社,1998.
[14]郑新奇.景观格局空间分析技术及其应用(第一版)[M].北京:科学出版社,2010.
[15]周放,赖月梅,曹指南,等.蛇类野外资源量调查方法——生境样方样带结合法[J].广西科学,1996,3(4):25-27.
[16]邹明泉,钟贻光.闽西北棘胸蛙生态调查及人工试养观察[J].动物学杂志,1986,21(3):4-8.
[17]Becker CG,Fonseca CR,Haddad CFB,et al. Habitat Split and the Global Decline of Amphibians[J].Science,2007,318:1775-1777.
[18]Blaustein A R. Chicken little or nero’s fiddle. A perspective on declining amphibian populations.Herpetologica,1994,50(1):85-97.
[19]Pounds JA,Crump ML. Amphibian declines and climate disturbance:the case the Colden Toad and the Harlequin Frog[J].Conservation Biology,1994,8(1)72-85.
[20]Pounds JA,Bustamante MR,Coloma LA,et al.Widespread amphibian extinctions from epidemic:disease driven by global warming[J].Nature,2006,439:161-167.
[21]International Union for Conservation of Nature(IUCN)(2000)Authority Files for Habitats&Threats.[2017-9-17].http://www.iucn.org/themes/ssc/sis/authority.html.
[22]Nitsehke. C R,Innes. J L. Integrating climate change into forest management in South Central British Columbia:An assessment of landscape vulnerability and development of a climate-smart framework[J].Forest Ecology And Management,2008,(256)3:313-327.
[2]董雅雯,佘济云,陈冬洋,等.基于箱线图的海南省东方市景观生态格局稳定性研究[J].中南林业科技大学学报,2016,36(8):104-108.
[3]费梁,胡淑琴.中国动物志两栖纲(中卷)无尾目[M].北京:科学出版社.2009.
[4]江建平,谢锋,臧春鑫,等.中国两栖动物受威胁现状评估[J].生物多样性,2016,24(5):588-597.
[5]廖常乐,王合升,黄娟,等.鹦哥岭自然保护区鹦哥岭树蛙种群分布及数量调查[J].动物学杂志,2013,48(3):377-381.
[6]潘晓赋,周伟,周用武,等.中国两栖类种群生态研究概述[J].动物学研究,2002,23(5):426-436.
[7]汪松,解焱.中国物种红色名录(第1卷红色名录)[M].北京:高等教育出版社.2004.
[8]王希臣,付梅臣,刘宗强,等.土地利用规划中建设用地需求量预测的两种模型比较—以东方市为例[J].资源与产业,2009,11(5):87-91.
[9]杨伟国.人工驯养棘胸蛙的繁殖研究[J].动物学杂志,1992,27(3):14-16.
[10]俞宝根.棘胸蛙不同地区的两性异形及人工环境下繁殖行为研究[D].杭州:浙江师范大学,2010.
[11]虞鹏程.赣东北棘胸蛙蝌蚪栖息地生物因子研究[J].四川动物,2000,19(3):163-164.
[12]杨保国.棘胸蛙的生态习性与人工养殖方法[J].生物学杂志,1990,(4):19-23.
[13]赵尔宓.中国濒危动物红皮书——两栖类和爬行类[M].北京:科学出版社,1998.
[14]郑新奇.景观格局空间分析技术及其应用(第一版)[M].北京:科学出版社,2010.
[15]周放,赖月梅,曹指南,等.蛇类野外资源量调查方法——生境样方样带结合法[J].广西科学,1996,3(4):25-27.
[16]邹明泉,钟贻光.闽西北棘胸蛙生态调查及人工试养观察[J].动物学杂志,1986,21(3):4-8.
[17]Becker CG,Fonseca CR,Haddad CFB,et al. Habitat Split and the Global Decline of Amphibians[J].Science,2007,318:1775-1777.
[18]Blaustein A R. Chicken little or nero’s fiddle. A perspective on declining amphibian populations.Herpetologica,1994,50(1):85-97.
[19]Pounds JA,Crump ML. Amphibian declines and climate disturbance:the case the Colden Toad and the Harlequin Frog[J].Conservation Biology,1994,8(1)72-85.
[20]Pounds JA,Bustamante MR,Coloma LA,et al.Widespread amphibian extinctions from epidemic:disease driven by global warming[J].Nature,2006,439:161-167.
[21]International Union for Conservation of Nature(IUCN)(2000)Authority Files for Habitats&Threats.[2017-9-17].http://www.iucn.org/themes/ssc/sis/authority.html.
[22]Nitsehke. C R,Innes. J L. Integrating climate change into forest management in South Central British Columbia:An assessment of landscape vulnerability and development of a climate-smart framework[J].Forest Ecology And Management,2008,(256)3:313-327.