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放牧干扰下高寒草甸物种多样性指数评价与选择
引用本文:牛钰杰,杨思维,王贵珍,刘丽,花立民. 放牧干扰下高寒草甸物种多样性指数评价与选择[J]. 生态学杂志, 2017, 28(6): 1824-1832. DOI: 10.13287/j.1001-9332.201706.026
作者姓名:牛钰杰  杨思维  王贵珍  刘丽  花立民
作者单位:甘肃农业大学草业学院/草业生态系统教育部重点实验室/中-美草地畜牧业可持续发展研究中心, 兰州 730070
基金项目:本文由国家自然科学基金项目(31460635)资助
摘    要:在青藏高原东北缘高寒草甸设置6个放牧强度样地,连续4年研究10个多样性指数(Richness和Abundance 2个实测指数,优势度指数、均匀度指数、丰富度指数和综合指数各2个)对放牧强度和年限影响植物群落的解释能力.结果表明: 相对于重要值,利用多度计算的多样性指数对放牧干扰更敏感.优势度指数(Berger-Parker、Dominance)与放牧强度和年限均无关,不能将放牧干扰对群落优势种的影响有效区分.均匀度指数(Equitability、Evenness)均与放牧强度无关,但Evenness指数与放牧年限呈显著负相关,不受偶见种影响且与物种多度的变异系数呈显著正相关,在基于时间尺度的均匀度比较中可以选择Evenness指数.丰富度指数(Menhinick、Margalef)均与放牧年限无关,但Margalef指数与放牧强度呈显著正相关,且不受偶见种影响.综合指数(Shannon、Simpson)均与放牧强度无关,但Shannon指数与物种丰富度和多度呈显著正相关,且随放牧年限增加而显著升高,不受偶见种影响,Shannon指数可用于在长时间尺度下比较物种多样性变化.在所有多样性指数中,只有实测物种丰富度和多度均与放牧强度呈显著负相关,与放牧年限呈显著正相关,且不受偶见种影响,故实测物种丰富度和多度相结合可作为放牧干扰下多样性比较的首选指标.此外,多样性指数选择须考虑放牧干扰的强度与时间特征、多样性组分和研究目的.

关 键 词:高寒草甸  放牧干扰  多样性指数
收稿时间:2016-10-18

Evaluation and selection of species diversity index under grazing disturbance in alpine mea-dow
NIU Yu-jie,YANG Si-wei,WANG Gui-zhen,LIU Li,HUA Li-min. Evaluation and selection of species diversity index under grazing disturbance in alpine mea-dow[J]. Chinese Journal of Ecology, 2017, 28(6): 1824-1832. DOI: 10.13287/j.1001-9332.201706.026
Authors:NIU Yu-jie  YANG Si-wei  WANG Gui-zhen  LIU Li  HUA Li-min
Affiliation:College of Grassland Science, Gansu Agricultural University/Ministry of Education Key Laboratory of Grassland Ecosystem/Sino-USA Center for Grazing Land Ecosystem Sustainability, Lanzhou 730070, China
Abstract:The research selected the plots of six grazing intensities in an alpine meadow in north-eastern Tibet Plateau in four years (2012-2015) and studied the relation between ten species diversity indexes, including two measured indexes (Richness and Abundance) in field and two indexes of each dominance, evenness, richness, integrated indexes, and grazing intensity as well as grazing time aiming at scientific selection of biodiversity index under grazing disturbance. The results indicated that the abundance was a better index than importance value to calculate biodiversity level because it was more sensitive to grazing disturbance. Dominance indexes, including Berger-Parker and Dominance, were not sensitive to grazing intensity and grazing time because they could not clarify the effect of grazing disturbance on dominant species in plant community. Evenness indexes, including Equitability and Evenness, had not relation with grazing intensity, however, the evenness index had a negative correlation with grazing time and it was not influenced by occasional species as well as the variation coefficient of species abundance. Hereby, the evenness index could be chosen for studying evenness change at temporal scale. Richness indexes, including Menhinick and Margalef, had no relation with grazing time, however, the Margalef index had a positive correlation with grazing intensity and the index was not influenced by occasional species. Integrated index, including Shannon and Simpson indexes, had no relation with grazing intensity, however, the Shannon index had a significant positive correlation with species richness and abundance and the index was not influenced by occasional species, and it significantly increased along grazing time. Hereby, Shannon index could be used as an index of studying plant species diversity in long-term. In ten diversity indexes, only the measured indexes in field, including richness and abundance, were signifi-cantly negatively correlated with grazing intensity, and positively correlated with grazing time, and the two indexes were not influenced by occasional species. Hereby, the combination of species richness and abundance mea-sured in field could be considered as the most important indexes for studying plant species diversity under grazing disturbance. Besides, the selection of biodiversity indexes must consider the spatial-temporal feature of grazing, diversity components and research purpose.
Keywords:alpine meadow  grazing disturbance  diversity index
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