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滨海自然植物群落物种多样性及种间垂直联结性
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  • 英文篇名:Species Diversity and Inter-specific Association between Vertical Layers in Coastal Natural Plant Communities
  • 作者:张艺帆 ; 任哲 ; 邓荣艳 ; 谢伟 ; 单笑旋
  • 英文作者:ZHANG Yifan;REN Zhe;DENG Rongyan;XIE Weidong;SHAN Xiaoxuan;College of Forestry,Guangxi University;
  • 关键词:滨海地区 ; 植物群落 ; 物种多样性 ; 垂直层次 ; 优势种 ; 种间联结
  • 英文关键词:coastal zone;;plant communities;;species diversity;;vertical layers;;dominant species;;inter-specific association
  • 中文刊名:GXKK
  • 英文刊名:Guangxi Sciences
  • 机构:广西大学林学院;
  • 出版日期:2019-06-19 08:30
  • 出版单位:广西科学
  • 年:2019
  • 期:v.26;No.113
  • 基金:国家自然科学基金项目(20120614);; 广西自然科学基金项目(0832030)资助
  • 语种:中文;
  • 页:GXKK201903009
  • 页数:11
  • CN:03
  • ISSN:45-1206/G3
  • 分类号:76-86
摘要
通过对滨海植物群落物种多样性和种间联结性研究,探索群落的形成及种间的共生与竞争关系,为滨海沙地和海岛修复的树种选择与配置提供理论依据。以广西防城港市滨海自然植物群落为对象,研究其群落结构、物种多样性及垂直层次间物种的联结性与相关性。结果表明:广西防城港滨海自然森林群落组成复杂,物种丰富,分层比较明显,大致可分为乔木层(含乔木层和亚乔木层)、灌木层和草本层。各物种丰富度指数(S)、Shannon-Wiener指数(H')、Simpson指数(D)和Pielou均匀度指数(Jsw)均表现为灌木层>乔木层>草本层,三者变化趋势较为一致,草本层处于退化状态;!2统计量、种间关联系数AC和物种共同出现百分率PC检验结果表明,乔木层与亚乔木层物种总体存在显著负联结,相互独立的种对较多,较少种对显著联结;乔木层与灌木层物种总体存在显著正联结,显著联结的种对较多,种对间较紧密;亚乔木层与灌木层物种间总体存在显著负联结,处于不稳定的演替阶段。表明群落内垂直层次间物种相似的生境要求、生态习性,以及在垂直方向上对生境要求的互补性差异是导致种对间关系的主要原因。
        Through the study of species diversity and inter-specific association of coastal plant communities,the formation of communities and the symbiotic and competitive relationship between species were explored,which provided a theoretical basis for the selection and allocation of tree species for coastal sandy land and island restoration. The coastal natural plant community in Fangchenggang City of Guangxi Province was taken as object,and the community structure,species diversity and the association and correlation of species between vertical layers were studied. The results show that the coastal natural forest community of Fangchenggang in Guangxi has complex composition,abundant species and obvious stratification. It can be roughly divided into tree layer( including tree and sub-tree layers),shrub layer and herb layer. The species richness index( S),Shannon-Wiener index( H'),Simpson diversity index( D) and Pielou evenness index( Jsw) were all expressed as shrub layer > tree and sub-tree layers > herb layer. The variation trend of species diversity index was consistent with the variation trend of richness index. The herb layer was in a state of degradation. The results of χ2 tests,inter-species association coefficient( AC) and percentage co-occurrence( PC)showed that there was significant negative association between tree layer and sub-tree layer,while there were more independent species pairs,and fewer pairs were significantly connected. There was a significant positive association between the species in tree layer and shrub layer,and there were more pairs of species that were significantly connected,and the species pairs were much closer. Generally there was a significant negative association between the species in sub-tree layer and shrub layer,which was in an unstable stage of succession. The results suggested that similar habitat requirements and ecological habits of species between vertical levels within a community and complementary differences in habitat requirements between the vertical layers might be the main driver affecting the relationship between species.
引文
[1]ODUM E P.Fundamentals of ecojogy[M].2nd ed.Pennysyvania:Cengage Learning,1980.
    [2]ALMADA F,CARPI P,CARLOS F F,et al.Identification of adult and juvenile Atherina presbyter Cuvier,1829 in a marine coastal area adjacent to Tagus estuary(NE Atlantic):A molecular tool for an ecological question[J].Journal of Applied Ichthyology,2017,33(2):168-173.
    [3]GUO H,WEAVER C,CHARLES S P,et al.Coastal regime shifts:Rapid responses of coastal wetlands to changes in mangrove cover[J].Ecology,2017,98(3):762-772.
    [4]HAMILTON S,CASEY D.Creation of a high spatiotemporal resolution global database of continuous mangrove forest cover for the 21st century(CGMFC-21)[J].Global Ecology and Biogeography,2016,25(6):729-738.
    [5]MALAVASI M,BARTAK V,CARRANZA M L,et al.Landscape pattern and plant biodiversity in Mediterranean coastal dune ecosystems:Do habitat loss and fragmentation really matter?[J].Journal of Biogeography,2018,45(6):1367-1377.
    [6]JARVIS S G,ROWE E C,HENRYS P A,et al.Empirical realised niche models for British coastal plant species[J].Journal of Coastal Conservation,2016,20(2):107-116.
    [7]üLLAS E,PEEP K,KALJU H.Land cover types and ecological conditions of the Estonian coast[J].Journal of Coastal Conservation,2002,8:109.
    [8]张磊,吴莺,王菲,等.红树林植物的研究进展[J].海峡药学,2014,26(4):8-12.
    [9]刘富强.山东省沙质海岸防护林群落多样性及其土壤理化性质研究[D].泰安:山东农业大学,2009.
    [10]覃莉.广西滨海红鳞蒲桃营养状况及其林地土壤理化性质研究[D].南宁:广西大学,2010.
    [11]王红丽,李艳丽,张文佺,等.崇明东滩湿地土壤养分的分布特征及其环境效应[J].环境科学与技术,2010,33(1):1-5.
    [12]罗弼樱,黄承标,闭炳翠,等.广西滨海红鳞蒲桃群落的土壤理化性质[J].亚热带农业研究,2016,12(3):175-180.
    [13]宿少锋,陈毅青,薛杨,等.海南岛滨海台地5种典型林分类型土壤理化特性研究[J].广东农业科学,2016,43(11):64-69.
    [14]高伟,叶功富,游水生,等.海岸沙地不同干扰方式植物群落结构与多样性[J].福建林学院学报,2011,31(3):227-233.
    [15]谢伟东,招礼军,邓荣艳,等.干扰对红鳞蒲桃群落植物多样性及重要值的影响[J].西南大学学报:自然科学版,2011,33(6):58-63.
    [16]曾聪,李蕾鲜,范航清.广西滨海红鳞蒲桃资源现状与群落特征[J].广西科学,2011,18(3):283-288.
    [17]赵艳云,陆兆华,刘京涛,等.海岸沙丘植物群落分布、适应性和演替研究进展[J].湿地科学,2014,12(3):401-408.
    [18]曾聪,李蕾鲜.25年来广西滨海红鳞蒲桃群落的变化特征[J].广西科学,2017,24(5):468-473.
    [19]李远发,王磊,喻素芳,等.广西滨海过渡区红鳞蒲桃群落的空间结构特征[J].生态学杂志,2016,35(3):726-732.
    [20]王伯荪,彭少麟.南亚热带常绿阔叶林种间联结测定技术研究Ⅰ.种间联结测式的探讨与修正[J].植物生态与地植物学丛刊,1985,9(4):274-285.
    [21]张金屯,焦蓉.关帝山神尾沟森林群落木本植物种间联结性与相关性研究[J].植物研究,2003,23(4):458-463.
    [22]张倩媚,陈北光,周国逸.鼎湖山主要林型优势树种种间联结性的计算方法研究[J].华南农业大学学报,2006,27(1):79-83.
    [23]黄云鹏.武夷山米槠林主要树种种间关联性[J].山地学报,2008,26(6):692-698.
    [24]康丽丹.暖温带落叶阔叶林灌木层种间关联探究[D].兰州:西北师范大学,2011.
    [25]刘金福,洪伟,樊后保,等.天然格氏栲林乔木层种群种间关联性研究[J].林业科学,2001,37(4):117-123.
    [26]王乃江,张文辉,陆元昌,等.陕西子午岭森林植物群落种间联结性[J].生态学报,2010,30(1):67-78.
    [27]潘高,张合平,潘登.中亚热带南酸枣林优势种群的种间联结性[J].生态学杂志,2017,36(4):892-901.
    [28]张志勇,陶德定,李德铢.五针白皮松在群落演替过程中的种间联结性分析[J].生物多样性,2003,11(2):125-131.
    [29]柴勇,孟广涛,武力,等.馨香玉兰所在群落主要树种的种间联结性[J].西北林学院学报,2009,24(5):31-35.
    [30]彭少麟,周厚诚,郭少聪,等.鼎湖山地带性植被种间联结变化研究[J].植物学报,1999,41(11):1239-1244.
    [31]周先叶,王伯荪,李鸣光,等.广东黑石顶自然保护区森林次生演替过程中群落的种间联结性分析[J].植物生态学报,2000,24(3):332-339.
    [32]邓莉萍,白雪娇,李露露,等.辽东山区次生林优势木本植物种间联结与相关分析[J].生态学杂志,2015,34(6):1473-1479.
    [33]戈峰.现代生态学[M].第2版.北京:科学出版社,2008.
    [34]张金屯.植被数量生态学方法[M].北京:中国科学技术出版社,1995.
    [35]马克平,黄建辉,于顺利,等.北京东灵山地区植物群落多样性的研究Ⅱ丰富度、均匀度和物种多样性指数[J].生态学报,1995,15(3):268-277.
    [36]黄忠良,孔国辉,何道泉.鼎湖山植物群落多样性的研究[J].生态学报,2000,20(2):193-198.
    [37]SCHLUTER D.A variance test for detecting species associations,with some example applications[J].Ecology,1984,65(3):998-1005.
    [38]张金屯.数量生态学[M].第2版.北京:科学出版社,2011.
    [39]宋贤利,邢福武,易绮婓,等.澳门松山阴香群落特征及物种多样性研究[J].福建林业科技,2013(3):1-7,13.
    [40]赵珊珊,曾庆文,邢福武.澳门青洲山血桐群落特征及物种多样性研究[J].安徽农业科学,2010,38(6):3243-3248.
    [41]彭少麟,王伯荪.鼎湖山森林群落分析Ⅰ.物种多样性[J].生态科学,1983,1:11-17.
    [42]邓贤兰,刘玉成,吴杨.井冈山自然保护区栲属群落优势种群的种间联结关系研究[J].植物生态学报,2003,27(4):531-536.
    [43]胡文强,黄世能,李家湘,等.南岭石坑崆山顶矮林乔木优势种群的种间关联性[J].生态学杂志,2013,32(10):2665-2671.
    [44]张明霞,王得祥,康冰,等.秦岭华山松天然次生林优势种群的种间联结性[J].林业科学,2015,51(1):12-21.
    [45]周刘丽,张晴晴,赵延涛,等.浙江天童枫香树群落不同垂直层次物种间的联结性与相关性[J].植物生态学报,2015,39(12):1136-1145.
    [46]张文辉,徐学华,李登武,等.黄土高原丘陵沟壑区狼牙刺群落恢复过程中的种间联结性研究[J].西北植物学报,2004,24(6):1018-1023.
    [47]农友,郑路,贾宏炎,等.广西大青山南亚热带森林植物群落的种间联结性[J].广西植物,2016,36(7):848-858.
    [48]郭忠玲,马元丹,郑金萍,等.长白山落叶阔叶混交林的物种多样性、种群空间分布格局及种间关联性研[J].应用生态学报,2004,15(11):2013-2018.
    [49]王文进,张明,刘福德,等.海南岛吊罗山热带山地雨林两个演替阶段的种间联结性[J].生物多样性,2007,15(3):257-263.
    [50]PETERSON C J,SQUIERS E R.An unexpected change in spatial pattern across 10 years in an aspen-white-pine forest[J].Journal of Ecology,1995,83(5):847-855.
    [51]刘春生,刘鹏,张志祥,等.九龙山南方铁杉群落物种多样性及乔木种种间联结性[J].生态环境学报,2008,17(4):1533-1540.
    [52]康冰,刘世荣,温远光,等.广西大青山南亚热带次生林演替过程的种群动态[J].植物生态学报,2006,30(6):931-940.

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