黄河下游平原农业景观异质性对两栖类生物栖息地可用性的影响

doi:10.13287/j.1001-9332.201607.018

应用生态学报 ›› 2016, Vol. 27 ›› Issue (7): 2154-2160.doi: 10.13287/j.1001-9332.201607.018

• 第八届全国景观生态学学术研讨会专栏 • 上一篇下一篇

黄河下游平原农业景观异质性对两栖类生物栖息地可用性的影响

张丽^1,2, 梁国付^1,2*, 郭豪杰^1,2, 李成蹊^1,2, 孙博琳^1,2, 卢训令^1,2, 丁圣彦^1,2

¹教育部黄河中下游数字地理技术重点实验室, 河南开封 475004;
²河南大学环境与规划学院, 河南开封 475004

收稿日期:2015-11-26 发布日期:2016-07-18
通讯作者: *E-mail: liangguofu@126.com
作者简介:张丽,女,1990年生,硕士研究生.主要从事景观生态学研究. E-mail: zhangli090303@126.com
基金资助:
本文由国家自然科学基金项目(41471146)和河南省高校青年骨干教师计划项目(2012GGJS-031)资助

Effects of landscape heterogeneity on the availability of amphibians’ habitats in agricultural region on the lower reaches of the Yellow River, China.

ZHANG Li^1,2, LIANG Guo-fu^1,2*, GUO Hao-jie^1,2, LI Cheng-xi^1,2, SUN Bo-lin^1,2, LU Xun-ling^1,2, DING Sheng-yan^1,2

¹Key Laboratory of Geospatial Technology for the Middle and Lower Yellow River Regions, Ministry of Education, Kaifeng 475004, Henan, China;
²College of Environment and Planing, Henan University, Kaifeng 475004, Henan, China

Received:2015-11-26 Published:2016-07-18
Contact: *E-mail: liangguofu@126.com
Supported by:
This work was supported by the National Natural Science Foundation of China (41471146) and the Foundation for University backbone Teachers of Henan Province, China (2012GGJS-031).

摘要/Abstract

摘要： 以黄河下游典型平原农业景观封丘县为研究区,基于图论的分析方法,采用概率连通性指数(PC)和斑块重要值(dPC_k)表征池塘栖息地可用性程度,在地理信息系统和R软件的支持下,分析了两栖类物种在250、500、1000和2000 m不同扩散能力下,反映池塘栖息地组成和构型的池塘平均面积(MS)以及池塘数量(NP)、至道路的最近距离(DR)组合作用对池塘栖息地可用性的影响.结果表明: 两栖类栖息地的可利用性与池塘数量、池塘平均面积和至道路的最近距离关系密切.在250 m扩散能力下,池塘平均面积和池塘数量是决定池塘可利用程度高低的重要影响因素;在500 m扩散能力下,池塘平均面积和至道路的最近距离对栖息地可用性的影响最为显著;在物种相对较高扩散能力下(1000和2000 m),池塘平均面积和池塘数量是最主要的影响因素.在平原农业景观中,两栖类生物及其栖息地的保护要充分考虑池塘斑块的数量、平均面积以及至道路的最近距离.

Abstract: SelectingFengqiu County in Henan Province, a typical region of the lower Yellow River, as the study area, adopting the analysis method of graph theory, with the support of geographic information systems (GIS) and R software, we analyzed the effects of landscape composition and landscape configuration, the mean pond size (MS), the number of ponds (NP), and distance to the nearest roads (DR), on habitat availability of amphibian species under different levels of dispersal ability (250, 500, 1000 and 2000 m), by referring the probability index of connectivity (PC) and the important value of patches (percentage of the variation in PC, dPC_k) to the degree of availability of ponds for amphibians’ breeding. The results indicated that the ponds availability for amphibians’ breeding was closely related to MS, NP, and DR. Therein, MS and NP were the key factors determining the availability of ponds under the dispersal ability of 250 m, and then MS and DR were the most significant influencing factors on pond availability under the dispersal ability of 500 m. However, under the high dispersal ability (1000 and 2000 m), MS and NP were the most important factors determining the availability of ponds. Therefore, with regard to the protection of amphibian species and their habitats in plain agricultural landscape, the number, mean size, and distances to the nearest roads of ponds should be taken into full consideration.

张丽, 梁国付, 郭豪杰, 李成蹊, 孙博琳, 卢训令, 丁圣彦. 黄河下游平原农业景观异质性对两栖类生物栖息地可用性的影响[J]. 应用生态学报, 2016, 27(7): 2154-2160.

ZHANG Li, LIANG Guo-fu, GUO Hao-jie, LI Cheng-xi, SUN Bo-lin, LU Xun-ling, DING Sheng-yan. Effects of landscape heterogeneity on the availability of amphibians’ habitats in agricultural region on the lower reaches of the Yellow River, China.[J]. Chinese Journal of Applied Ecology, 2016, 27(7): 2154-2160.

参考文献

[1] Lu X-L (卢训令), Liang G-F (梁国付), Tang Q (汤茜), et al. Plant species of the non-agricultural habitats in the lower reaches of the Yellow River plain agro-landscape. Acta Ecologica Sinica (生态学报), 2014, 34(4): 789-797 (in Chinese)
[2] Yu Z-R (宇振荣), Gu W-B (谷卫彬), Hu D-X (胡敦孝). On landscape pattern and biodiversity in rural areas of Jianghan Plain : Taking two villages as a case study. Resources Science (资源科学), 2000, 22(2): 19-23 (in Chinese)
[3] Lu X-L (卢训令), Tang Q (汤茜), Liang G-F (梁国付), et al. Plant species of the non-agricultural habitats in the lower reaches of the Yellow River Plain. Acta Ecologica Sinica (生态学报), 2015, 35(5): 1527-1536 (in Chinese)
[4] Semlitsch, RD. Critical elements for biologically based recovery plans of aquatic-breeding amphibians. Conservation Biology, 2002, 16: 619-629
[5] Zhou ZZ. Landscape changes in a rural area in China. Landscape and Urban Planning, 2000, 47: 33-38
[6] Gibbs JP. Distribution of woodland amphibians along a forest fragmentation gradient. Landscape Ecology, 1998, 13: 263-268
[7] Becker CG, Fonseca CR, Haddad CFB, et al. Habitat split and the global decline of amphibians. Science, 2007, 318: 1775-1777
[8] Saunders DA, Hobbs RJ, Margules CR. Biological consequences of ecosystem fragmentation: A review. Conservation Biology, 1991, 5: 18-32
[9] Wake DB, Vredenburg VT. Are we in the midst of the sixth mass extinction? A view from the world of amphibians. Proceedings of the National Academy of Sciences of the United States of America, 2008, 105: 11466-11473
[10] Werner EE, Yurewicz KL, Skelly DK, et al. Turnover in an amphibian metacommunity: The role of local and regional factors. Oikos, 2007, 116: 1713-1725
[11] Pillsbury FC, Miller JR. Habitat and landscape characteristics underlying anuran community structure along an urban-rural gradient. Ecological Applications, 2008, 18: 1107-1118
[12] Stuart SN, Chanson JS, Cox NA, et al. Status and trends of amphibian declines and extinctions worldwide. Science, 2004, 306: 1783-1786
[13] Knutson MG, Richardson WB, Reineke DM, et al. Agricultural ponds support amphibian populations. Ecological Applications, 2004, 14: 669-684
[14] Schmidt BR, Pellet J. Relative importance of population processes and habitat characteristics in determining site occupancy of two anurans. Journal of Wildlife Management, 2005, 69: 884-893
[15] Saura S, Pascual-Hortal L. A new habitat availability index to integrate connectivity in landscape conservation planning: Comparison with existing indices and application to a case study. Landscape and Urban Planning, 2007, 83: 91-103
[16] Bowne DR, Bowers MA. Interpatch movements in spatially structured populations: A literature review. Landscape Ecology, 2004, 19: 1-20
[17] Houlahan JE, Findlay CS, Schmidt BR, et al. Quantitative evidence for global amphibian population declines. Nature, 2000, 404: 752-755
[18] Semlitsch RD, Bodie JR. Biological criteria for buffer zones around wetlands and riparian habitats for amphibians and reptiles. Conservation Biology, 2003, 17: 1219-1228
[19] Wu S-H (吴淑辉), Zhai W-Y (瞿文元). A preliminary study of the amphibian fauna of Henan Province. Journal of Xinxiang Normal College (Natural Science) (新乡师范学院学报:自然科学版), 1984(1): 89-93 (in Chinese)
[20] Shi L (石灵), Hou M-G (侯名根), Wang X-W (王新卫), et al. Protections and resources of amphibians in Jingangtai Nature Reserve, Henan Province. Sichuan Journal of Zoology (四川动物), 2011, 30(5): 828-830 (in Chinese)
[21] Xia Z-R (夏中荣), Chen X-H (陈晓虹), Liang J-B (梁俊波). A survey on diversity of amphibians in Funiu Mountain, Henan. Sichuan Journal of Zoology (四川动物), 2006, 25(2): 307-311 (in Chinese)
[22] Smith MA, Green DM. Dispersal and the metapopulation paradigm in amphibian ecology and conservation: Are all amphibian populations metapopulations? Ecography, 2005, 28: 110-128
[23] Saura S, Pascual-Hortal L. A new habitat availability index to integrate connectivity in landscape conservation planning: Comparison with existing indices and application to a case study. Landscape and Urban Planning, 2007, 83: 91-103
[24] Saura S, Rubio L. A common currency for the different ways in which patches and links can contribute to habitat availability and connectivity in the landscape. Ecography, 2010, 33: 523-537
[25] Decout S, Manel S, Miaud C, et al. Integrative approach for landscape-based graph connectivity analysis: A case study with the common frog (Rana temporaria) in human-dominated landscapes. Landscape Ecology, 2012, 27: 267-279
[26] Wu C-G (吴昌广), Zhou Z-X (周志翔), Wang P-C (王鹏程), et al. Evaluation of landscape connectivity based on least-cost model. Chinese Journal of Applied Ecology (应用生态学报), 2009, 20(8): 2042-2048(in Chinese)
[27] Liu C-F (刘常富), Zhou B (周彬), He X-Y (何兴元), et al. Selection of distance thresholds of urban forest landscape connectivity in Shenyang City. Chinese Journal of Applied Ecology (应用生态学报), 2010, 21(10): 2508-2516 (in Chinese)
[28] Angelone S, Kienast F, Holderegger R. Where movement happens: Scale-dependent landscape effects on genetic differentiation in the European tree frog. Ecography, 2011, 34: 714-722
[29] Pellet J, Hoehn S, Perrin N. Multiscale determinants of tree frog (Hyla arborea L.) calling ponds in western Switzerland. Biodiversity and Conservation, 2004, 13: 2227-2235
[30] Vos CC, Stumpel AHP. Comparison of habitat-isolation parameters in relation to fragmented distribution patterns in the tree frog (Hyla arborea). Landscape Ecology, 1996, 11: 203-214
[31] Clauzel C, Girardet X, Foltête JC. Impact assessment of a high-speed railway line on species distribution: Application to the European tree frog (Hyla arborea) in Franche-Comté. Journal of Environmental Management, 2013, 127: 125-134
[32] Burnham KP, Anderson DR. Model Selection and Multimodel Inference: A Practical Information-theoretic Approach. Berlin: Springer Science and Business Media, 2002
[33] Grueber CE, Nakagawa S, Laws RJ, et al. Multimodel inference in ecology and evolution: Challenges and solutions. Journal Evolutionary Biology, 2011, 24: 699- 711
[34] Cushman SA. Effects of habitat loss and fragmentation on amphibians: A review and prospectus. Biological Conservation, 2006, 128: 231-240
[35] Pearman PB. Effects of pond size and consequent predator density on two species of tadpoles. Oecologia, 1995, 102: 1-8
[36] Gibbs JP. Distribution of woodland amphibians along a forest fragmentation gradient. Landscape Ecology, 1998, 13: 263-268
[37] Parris KM. Urban amphibian assemblages as metacommunities. Journal of Animal Ecology, 2006, 75: 757-764
[38] Etienne RS. On optimal choices in increase of patch area and reduction of interpatch distance for metapopulation persistence. Ecological Modelling, 2004, 179: 77-90
[39] Hodgson JA, Thomas CD, Cinderby S, et al. Habitat recreation strategies for promoting adaptation of species to climate change. Conservation Letters, 2011, 4: 289-297
[40] McRae BH, Hall SA, Beier P, et al. Where to restore ecological connectivity? Detecting barriers and quantifying restoration benefits. PLoS One, 2012, 7(12): e52604

黄河下游平原农业景观异质性对两栖类生物栖息地可用性的影响

Effects of landscape heterogeneity on the availability of amphibians’ habitats in agricultural region on the lower reaches of the Yellow River, China.

PDF (PC)

可视化

摘要/Abstract

引用本文

使用本文

参考文献

相关文章 0

编辑推荐

Metrics

本文评价