黔中喀斯特山地森林灌木层结构与功能研究
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摘要
本文以黔中喀斯特山地森林灌木层为主要研究对象,采用标准地调查和取样分析、外业调查和内业研究、定性描述和定量分析相结合的方法,应用计算机分析系统软件进行数据处理,系统研究了黔中喀斯特山地森林群落灌木层的结构与功能。主要研究结果如下:
     灌木层植物种类丰富,植物区系起源古老,具有温带区系与热带区系并重的特点。根据灌木层物种组成,55个样地被分为15种群落类型,在类型基础上根据乔木层物种组成划分亚类。灌木层群落的外貌主妻是由小型和中型落叶草质及常绿革质、非全缘单叶的高位芽植物组成。灌木层群落物种多样性指数、均匀度指数和丰富度指数之间呈正相关关系,针阔叶混交林物种多样性最高,阔叶林次之,针叶林最低,种多样性指数(2.7975)、种丰富度指数(0.6261)、生态优势度指数(0.2023)、种间机遇率(0.8089)、多样性指数(2.1304)、均匀度指数(0.7753)在各群落类型中呈现出比较一致的变化趋势。灌木层片主要由白栎、香叶树、茅栗、杜鹃、铁仔、川榛、金佛山荚蒾等组成,重要值分别为8.7748、4.7059、3.8524、3.2543、3.1876、2.4199、2.0879,盖度60%左右,平均高1.65m,平均胸径1.25cm,密度32625株/ha,叶量1.5663T/ha,生物量7.0386T/ha。试验区主要元素中Ca、N平均含量最高,分别为37.5362Kg/hm~2、17.2046Kg/hm~2,K、Mg次之,分别为3.8024Kg/hm~2、2.686Kg/hm~2,P平均含量最低,为0.9289Kg/hm~2。马尾松-枫香+铁仔+白栎群落的平均高度、平均胸径及生物量最小,密度、叶量及元素含量最大,珊瑚树+复羽栾树-珊瑚树群落的平均高度、平均胸径最大,杨梅+白栎-满山红群落的生物量最大,马尾松+杉木+白杨+白栎-白栎群落的叶量最小,枫香+杉木+马尾松-香叶树群落的密度及元素含量最小。
     试验区乔木层植物共42科72属106种,灌木层植物共67科148属292种,在乔、灌层同时出现的有28科47属55种。灌木层平均高度、平均地径和生物量分别比乔木层小6.5m、10.201cm和106.572T/ha、密度比乔木层大31439株/ha。乔灌层的N、P、K、Ca、Mg含量分别为412.6231kg/ha、39.8209kg/ha、264.4192kg/ha、926.0364kg/ha、225.3816kg/ha,其中,灌木层含量分别占4.17%、2.33%、1.44%、4.05%、1.19%。灌木层平均高度比草本层大1.38m、密度比草本层小135748株/ha。灌草层的N、P、K、Ca、Mg含量分别为32.5051kg/ha、2.0916kg/ha、14.1965kg/ha、45.3259kg/ha、5.8252kg/ha,其中,灌木层含量分别占52.92%、44.43%、28.78%、82.81%、46.11%。灌木层的高度随着乔木层高度、胸径、密度增大而减小、生物量增大而增大,森林群落处于发育-恢复期,随着草本层高度增加而增加、密度及生物量增加而减小。灌木层的地径随着乔木层高度、胸径、密度及生物量的增加而减小。灌木层的密度随着乔木层高度、胸径、密度及生物量的增加而增加,随着草本层高度及生物量增加而减小、密度增加而增加。灌木层的生物量随乔木层高度、密度及生物量增加而增加、胸径增加而减小,随草本层高度及生物量增加而减小、密度增加而增加。灌木层的元素含量随草本层元素含量增加而增加。黔中喀斯特山地海拔在602m至1610m之间,分布有较多陡峻山岭,相对高差可达400~500m,受外部环境影响小,灌木层群落较为稳定,灌木层植物在中等海拔高度、东、南坡向、坡度较小和大的坡下部发育较好。
     本研究较全面地分析了黔中喀斯特山地森林灌木层的结构与功能,可以为黔中喀斯特山地植被恢复、资源管理、植被保护等提供理论依据。
This artical takes the structure and function of the shrub layer in Guizhou provincial central karst mountainous areas as the research object.Using the methods of field plot investigation,combined with field investigation and inner analysis,qualitative and quantitative method,structure and function of the shrub layer in Guizhou provincial central karst mountainous areas was researched deeply.The data handling was carried out by computer analysis system.The main results as follows:
     The plant of shrub layer is rich in comprising species,complex in geographical elements, having an extensive connection with nearby floristic areas.The floristic characteristic of the region emphasizes on the tropical flora as well as the temperate flora.55 plots were divided into 15 community through the plants of shrub layer.The physiognomy of the community of shrub layer is mainly decided by the phanerophytes with microphylls,mesophylls,herbaceous, deciduous and evergreen leathery,simple and unentire leaves.In the community of shrub layer, the species diversity index,evenness index and richness index have pure correlational dependence. Gleason index is 2.7975.Menhinnick index is 0.6261.Simpson index is 0.2023.Hurlbert index is 0.8089.Shannon-Wiener index is 2.1304.Pielou index is 0.7753.The plants of shrub layer were mainly composed of Quercus fabric(8.7748),Lindera communis Hems l(4.7059),Castanea sequinii Dode(3.8524),Rhododendron simsii Planch(3.2543),Myrsine africana Linn(3.1876), Corylus heterophylla Fisch.ex Bess.var.sutchuenensis Franch(2.4199),Viburnum chinshanense Graeb(2.0879) and so on.The shrub layer coverage rate is 60%,average high is 1.65m,average DBH is 1.25era,biomass is 1.5663T/ha,leaf weight is 7.0386T/ha,and there are 32625 plants per hectare.In karst mountainous region in Guizhou provincial center,the contents of N,P,K,Ca and Mg are 17.2046Kg/hm~2,0.9289Kg/hm~2,3.8024Kg/hm~2,37.5362Kg/hm~2 and 2.686Kg/hm~2, respectively.In Pinus massoniana Lamb-Liquidambar formosana Hance,average high,DBH and leaf weight of shrub layer are least,biomas and element weight are largest.In Celtis julianae Schneid+Koelreuteria bipinnata Franch-Celtis julianae Schneid,average high and DBH of shrub layer are largest,leaf weight of shrub layer is largest in Myrica rubra(Lour.) Sieb.et Zucc+Quercus fabric-Rhododendron mariesii Hemsl.et Wils.The biomas is least in Pinus massoniana Lamb+Cunninghamia lanceolata(Lamb.) Hook+Salicaceae SP+Quercus fabric-Quercus fabric.The density and element weight are least in Liquidambar formosana Hance+Cunninghamia lanceolata(Lamb.) Hook+Pinus massoniana Lamb-Lindera communis Hemsl.
     The interrelation between shrub layer and the other parts of ecosystem is complicated.There are 42 families,72 genus and 106 species in tree layer.There are 67 families,148 genus and 292 species in shrub layer.There are 28 families,47 genus and 55 species in tree and shrub layer.For the average high,average DBH and biomass,the shrub layer is lower 6.5m,10.201cm and 112.0433T/ha,respectively than the tree layer.For density,the shrub layer is higher 31439(plants per hectare) than the tree layer.There are 412.6231Kg N,39.8209Kg P,264.4192Kg K, 926.0364Kg Ca,225.3816Kg Mg per ha in the tree and shrub layer,and the ratio of the shrub layer is 4.17%,2.33%,1.44%,4.05%,1.19%,respectively.For the average high,the shrub layer is higher 1.38m than the herb layer.For density,the shrub layer is lower 135748(plants per hectare) than the herb layer.There are 32.5051kg N,2.0916kg P,14.1965kg K,45.3259kg Ca,5.8252kg Mg per ha in the shrub and herb layer,and the ratio of the shrub layer is 52.92%,44.43%, 28.78%,82.81%,46.11%,respectively.The high of shrub layer and the high,DBH,density of tree layer,density,biomass of herb layer is showing a diverse change tendency.The high of shrub layer and the biomass of tree layer,high of herb is showing a similar change tendency.The DBH of shrub layer and the high,DBH,density,biomass of tree layer is showing a diverse change tendency.The density of shrub layer and the high,DBH,density,biomass of tree layer,density of herb layer is showing a similar change tendency.The density of shrub layer and the density, biomass of herb layer is showing a diverse change tendency.The biomass of shrub layer and the high,density,biomass of tree layer,density of herb layer is showing a similar change tendency. The biomass of shrub layer and the DBH of tree layer,the high,biomass of herb layer is showing a diverse change tendency.A change of the contents of elements of shrub layer and herb layer is showing a similar tendency.In karst mountainous region in Guizhou provincial center,the plants of shrub layer will grow better at middle altitude,eastern and southern slopes,under-part of less and big gradient.
     we can comprehend the structure and function of the shrub layer in Guizhou provincial central karst mountainous areas through the research.It provides the theory basis for vegetation restores,resource administration and vegetation protection etc.
引文
[1]丁立仲等.千岛湖破碎化景观中灌木层植被的边缘效应.浙江大学学报(农业与生命科学版)[J],2006,32(5):563-568
    [2]马丹炜.九寨沟自然保护区次生林物种多样性分析.四川师范大学学报(自然科学版)[J],1999,22(1):83-87
    [3]马文翰.贵州喀斯特脆弱生态环境的可持续发展.贵州师范大学学报,2003,21:75-77
    [4]万军.贵州省喀斯特地区土地退化与生态重建研究进展.地球科学进展,2003,18:447-453
    [5]孔亮,陈祥伟.黑龙江省东部山地灌木林地的静态持水能力.山地学报[J],2005,23(5):626-630
    [6]孔亮,蒙宽宏等.黑龙江省东部山地灌木林土壤水分动态变化.东北林业大学学报[J],2005,33(5):44-46
    [7]王国荣,陈秀蓉等.东祁连山高寒灌丛土壤微生物的分布特征.草原与草坪[J],2006,3:27-30
    [8]王树森等.华北土石山区天然森林植被种间联结和生态位的研究.水土保持研究[J],2006,13(4):170-175
    [9]王新平,康尔泗等.荒漠地区主要固沙灌木的降水截留特征.冰川冻土[J],2004,26(1):89-94
    [10]王新平,李新荣等.干旱半干旱地区人工固沙灌木林生态系统演变特征.生态学报[J],2005,25(8):1974-1980
    [11]王永健等.茂县土地岭植被恢复过程中物种多样性动态特征.生态学报[J],2006,26(4):1028-1036
    [12]王志强,刘宝元,王晓兰.黄土高原半干旱区天然锦鸡儿灌丛对土壤水分的影响.地理研究[J],2005,24(1):113-119
    [13]王志泰.东祁连山柳灌丛群落物种多样性及干扰分析.山地农业生物学报[J],2005,24(1):22-28
    [14]王志泰等.东祁连山高寒草地柳灌丛群落种间关联性.生态学杂志[J],2006,25(10):1177-1180
    [15]中国植被编辑委员会.中国植被[M].北京:科学出版社,1980
    [16]冯宗炜,王效科,吴刚.中国森林生态系统的生物量[M].北京:科学出版社,1999
    [17]史军辉等.鼎湖山针阔混交林木本植物种群的空间分布特征.南京林业大学学报(自然科学版)[J],2006,30(5):34-38
    [18]史作民等.宝天曼地区栓皮栎林恢复过程中高等植物物种多样性变化.植物生态学报[J],1998,22(5)415-421
    [19]史作民等.宝天曼植物群落物种多样性研究.林业科学[J],2002,38(6):17-23
    [20]史作民等.宝天曼落叶阔叶林种间联结性研究.林业科学[J],2001,37(2):29-35
    [21]张德罡,胡自治.东祁连山杜鹃灌丛草地灌木种群分布格局研究.草地学报,2003,11(3):234-239
    [22]张峰,上官铁梁.翅果油树群落优势种群生态位分析.西北植物学报[J],2004,24(1):70-74
    [23]张光富,宋永昌.不同处理措施下浙江天童灌丛群落组成结构的变化.应用生态学报[J],2002,13(1):16-20
    [24]张桂萍等.山西绵山植被优势种群生态位研究.植物研究[J],2006,26(2):176-181
    [25]张华,何红等.科尔沁沙地灌木对风沙土壤的生态效应.地理研究 [J],2005,24(5):708-716
    [26]张金屯,陈廷贵.关帝山植物群落物种多样性研究.山西大学学报(自然科学版)[J],2002,25(2):173-175
    [27]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.植物研究[J],2003,23(4):458-463
    [28]张金屯.数量生态学[M].北京:科学出版社,2004
    [29]张锦春等.库姆塔格沙漠南缘荒漠植物群落多样性分析.植物生态学报[J],2006,30(3):375-382
    [30]张远东,刘世荣等.川西高山和亚高山灌丛的地被物及土壤持水性能.生态学报[J],2006,26(9):2775-2782
    [31]张志杰,张奎文.灌木在忻州林业生态建设中的作用[J].山西林业科技,2002,(增刊):34-35
    [32]毕润成等.吕梁山南端白皮松的群落特征及其多样性的研究.植物研究[J],2002,22(3):366-372
    [33]初玉,杨慧玲等.浑善达克沙地小叶锦鸡儿灌丛的空间异质性.生态学报[J],2005,25(12):3294-3300
    [34]刘长秀,张宏等.灌丛对川西北高寒草甸土壤资源的影响.山地学报[J],2006,24(3):357-365
    [35]刘创民等.北京九龙山灌丛植被的物种多样性分析.林业科学研究[J],1994,7(2):143-148
    [36]刘晋.准噶尔盆地荒漠区梭梭灌木林的自我修复能力研究.中国水土保持[J],2006,3:25-26
    [37]刘庆等.川西米亚罗亚高山地区云杉林群落结构分析.山地学报[J],2003,21(6):695-701
    [38]刘世荣,蒋有绪,史作民等.中国暖温带森林生物多样性研究[M].北京:中国科学技术出版社,1998
    [39]刘兴良,郝晓东等.卧龙巴郎山川滇高山栎灌丛地上生物量及其模型.生态学杂志[J],2006,25(5):487-491
    [40]刘兴良,刘世荣等.巴郎山川滇高山栎灌丛地上生物量及其对海拔梯度的响应.林业科学[J],2006,42(2):1-7
    [41]刘映良.喀斯特典型山地退化生态系统植被恢复研究(博士论文),2005
    [42]任海.喀斯特山地生态系统石漠化过程及其恢复研究综述.热带地理,2005,25(3):197-200
    [43]孙中伟,赵士洞.长白山北坡椴树阔叶红松林群落木本植物种间联结性与相关性研究.应用生态学报[J],1996,7(1):1-5
    [44]许皓,李彦.3种荒漠灌木的用水策略及相关的叶片生理表现.西北植物学报[J],2005,25(7):1309-1316
    [45]许文强,罗格平,陈曦.干旱区绿洲-荒漠过渡带灌丛土壤属性研究.应用生态学报[J],2006,17(4):583-586
    [46]阳含熙,卢泽愚.植物生态学的数量分类方法[M].北京:科学出版社,1981
    [47]朱守谦.喀斯特森林生态研究(ⅲ)[M].贵阳:贵州科学出版社,2003
    [47]阿拉木萨,蒋德明,骆永明.半干旱区人工固沙灌丛发育过程土壤水分及水量平衡研究.水土保持学报[J],2005,19(4):107-110
    [49]阿拉木萨,慈龙骏等.科尔沁沙地不同密度小叶锦鸡儿灌丛水量平衡研究.应用生态学 报[J],2006,17(1):31-35
    [50]陈红锋等.广州科学城灌丛群落特征与景观改造.中山大学学报(自然科学版)[J],2005,44:226-231
    [51]陈小红,段争虎等.兰州市南北两山人工灌木林地土壤水分动态.中国沙漠[J],2006,26(4):532-535
    [52]国家林业局.森林土壤分析方法.中华人民共和国林业行业标准LY/T1210~1275-1999.北京:中国标准出版社,2000
    [53]何东进等.常绿阔叶防护林优势树种生态相似关系研究.福建林学院学报[J],1999,19(2):138-141
    [54]何云核,叶海宾.安徽休宁县森林植物群落物种多样性分析.西北林学院学报[J],2001,16(1):9-11
    [55]李博.生态学[M].北京:高等教育出版社,2000
    [56]李红云,李焕平.4种灌木林地土壤物理性状及抗侵蚀性能的研究.水土保持学报[J],2006,20(3):13-16
    [57]李军玲等.关帝山亚高山灌丛草甸群落优势种群的生态位研究.西北植物学报[J],2003,23(12):2081-2088
    [58]李军玲等.关帝山亚高山灌丛群落和草甸群落优势种的种间关系.草地学报[J],2004,12(2):113-119
    [59]李品荣等.滇东南岩溶山地3种人工林群落林下植物群落学特征比较.热带亚热带植物学报[J],2006,14(4):287-293
    [60]李清河,江泽平等.灌木的生态特性与生态效能的研究与进展.干旱区资源与环境[J],2006,20(2):159-164
    [61]李新荣.俄罗斯平原针阔混交林群落的灌木层植物种间相关研究.生态学报[J],1999,19(1):54-60
    [62]李英年,赵亮等.高寒金露梅灌丛生物量及年周转量.草地学报[J],2006,14(1):72-76
    [63]李裕元,邵明安.子午岭植被自然恢复过程中植物多样性的变化.生态学报[J],2004,24(2):252-260
    [64]沈琪等.浙江省生态公益林植被恢复过程中物种组成及多样性的变化.生态学报[J],2005,25(9):2131-2138
    [65]汪万福,王涛等.敦煌莫高窟崖顶灌木林带防风固沙效应.生态学报[J],2004,24(11):2492-2500
    [66]吴大干等.昆嵛山森林群落下灌草层结构与多样性研究.山东大学学报(理学版)[J],2007,42(1):83-88
    [67]吴彦等.亚高山针叶林人工恢复过程中物种多样性变化.应用生态学报[J],2004,15(8):1301-1306
    [68]吴征镒.中国种子植物属的分布区类型[J].云南植物研究,1991,增刊Ⅵ:1-139
    [69]吴征镒,王荷生.中国自然地理.植物地理[M].北京:科学出版社,1983
    [70]吴征镒等.种子植物分布区类型及其起源和分化[M].昆明:云南科技出版社,2006.4
    [71]吴征镒等.中国被子植物科属综论[M].北京:科学出版社,2003
    [72]杨君珑等.子午岭油松林灌木层主要树种的空间分布格局和种间关联性研究.西北植物学报[J],2007,27(4):791-796
    [73]杨清培等.红壤丘陵区湿地松林下灌木层物种组成及主要种群间联结性研究.江西农业大学学报[J],2007,29(5):773-777
    [74]林伟强等.广州帽峰山次生林主要种群种间联结性研究.生态科学 [J],2004,23(1):42-46
    [75]林银森.华安贡鸭山森林群落物种多样性研究.江西农业大学学报[J],2003,25:113-118
    [76]柳江等.退化红壤区植被恢复过程中灌木层主要种群的生态位特征.植物资源与环境学报[J],2002,11(2):11-16
    [77]尚文艳等.辽西大黑山北坡植物群落组成及多样性研究.生态学杂志[J],2005,24(9):994-998
    [78]赵丽娅,李兆华等.流动沙丘先锋灌木差巴嘎蒿的种子散布格局[J].西北植物学报,2005,25(9):1821-1826
    [79]赵振勇,王让会等.天山南麓山前平原柽柳灌丛地上生物量.应用生态学报[J],2006,17(9):1557-1562
    [80]周厚诚等.广东南澳岛次生林的群落结构分析.广西植物[J],2001,21(3):209-214
    [81]周纪伦.植物种群生态学[M].北京:高等教育出版社,1992
    [82]周小勇等.鼎湖山针阔混交林演替过程中群落组成和结构短期动态研究.热带亚热带植物学报[J],2004,12(4):323-330
    [83]周政贤.贵州森林[M].贵州科技出版社,1992
    [84]郭雨华,赵廷宁等.灌木林对地表风况及空气动力学参数影响的野外调查研究-以丰宁满族自治县小坝子乡为例.林业调查规划[J],2006,31(4):72-75
    [85]郭正刚等.白龙江上游地区森林植物群落物种多样性的研究.植物生态学报[J],2003,27(3):388-395
    [86]胡胜华等.鄱阳湖砂山地区风沙化过程中物种多样性的变化.中国沙漠[J],2006,26(5):729-733
    [87]茹文明等.历山森林群落物种多样性与群落结构研究.应用生态学报[J],2006,17(4):561-566
    [88]茹文明等.山西霍山森林群落林下物种多样性研究.生态学杂志[J],2005,24(10):1139-1142
    [89]茹文明等.太行山南段森林群落物种多样性研究.西北植物学报[J],2006,26(5):1036-1042
    [90]高宝嘉等.残次油松林群落特征与生物多样性恢复.生态学报[J],1999,19(5):647-653
    [91]康冰等.南亚热带人工杉木林灌木层物种组成及主要木本种间联结性.生态学报[J],2005,25(9):2174-2179
    [92]栾文举,张三亮.甘肃省白水江自然保护区次生灌木林植物群落物种多样性研究.甘肃农业大学学报[J],2003.38(2):133-139
    [93]莫菲,陈训.贵州花江典型喀斯特峡谷天然灌丛植被的调查与分析.贵州科学[J],2004,22(3):83-85
    [94]徐秋芳,姜培坤,沈泉.灌木林与阔叶林土壤有机碳库的比较研究.北京林业大学学报[J],2005,27(2):18-22
    [95]袁素芬,陈亚宁等.新疆塔里木河下游灌丛地上生物量及其空间分布.生态学报[J],2006,26(6):1818-1824
    [96]袁穗波等.雪峰山西南支脉丘陵山地森林植物群落类型及结构特征研究.生态学杂志[J],2004,23(4):1-6
    [97]程瑞梅等.三峡库区灌丛群落多样性的研究.林业科学研究[J],2000,13(2):129-133
    [98]程占红,张金屯.生态旅游区不同距离带上植物群落的结构对比.应用与环境生物学报 [J],2002,8(1):8-13
    [99]董全民等.高寒小嵩草草甸暖季草场主要植物种群的生态位.生态学杂志[J],2006,25(11):1323-1327
    [100]董铁狮,赵雨森等.黑龙江东部榛子灌丛水源涵养功能研究.防护林科技[J],2006,2:3-5
    [101]韩胜利,叶冬梅等.乌兰布和沙漠白刺灌丛土壤水分及物理特性的研究.干旱区地理[J],2005,28(4):506-510
    [102]蒋齐,李生宝等.人工柠条灌木林营造对退化沙地改良效果的评价.水土保持学报[J],2006,20(4):23-27
    [103]蒋有绪.世界森林生态系统结构与功能的研究综述.林业科学究研究[J],1995,8(3):314-321
    [104]覃文更等.广西木论自然保护区青檀群落特征及其多样性研究.广西林业科学[J],2004,33(3):126-129
    [105]童丽丽等.南京牛首山南京椴群落的结构分析.南京林业大学学报(自然科学版)[J],2006,30(5):42-46
    [106]温远光.常绿阔叶林退化生态系统恢复过程物种多样性的发展趋势与速率.广西农业大学学报[J],1998,17(2):93-106
    [107]谢双喜,彭贵.贵州喀斯特山地灌丛香叶树群落及种群结构的初步研究.中南林业调查规划,2002(1):56-62
    [108]曾慧卿,刘琪璟等.千烟洲灌木生物量模型研究.浙江林业科技[J],2006,26(1):13-17
    [109]曾珍英等.灌木各测树因子相关性以及器官生物量相关性的研究.江西农业大学学报[J],2005,27(5):694-699
    [110]鲍文,包维楷.岷江上游中山区次生灌丛与人工油松林土壤理化性质比较研究.水土保持通报[J],2004,24(5):10-13
    [111]蔡哲,刘琪璟等.千烟洲试验区几种灌木生物量估算模型的研究,中南林学院学报[J],2006,26(3):15-19
    [112]雷相东等.东北过伐林灌木层物种多样性与林分因子的典型相关分析.应用与环境生物学报[J],2002,8(4):346-350
    [113]熊小刚,韩兴国.资源岛在草原灌丛化和灌丛化草原中的作用.草业学报[J],2006,15(1):9-14
    [114]霍竹,邵明安.黄土高原水蚀风蚀交错带降水及灌木林冠截留特性研究.干旱地区农业研究[J],2005,23(5):88-92
    [115]霍竹,邵明安.黄土高原水蚀风蚀交错带沟岸灌木林地土壤水分变化.农业工程学报[J],2005,21(6):45-49
    [116]Crawford C S.Desert ecosystems:their resources in space and time.Environmental conservation[J],1982,9:181-195
    [117]Gross K L.A comparison of methods for estimating seed numbers in the soil[J].Journal of ecology,1990,78:1079-1093
    [118]Hanley M E.Seed size and germination response:a relationship for fire-following plant species exposed to thermal shoek[J].Oecologia,2003,134:18-22
    [119]Harrison,S.Local and regional diversity in a partly landscape:native,alien and endemic herbs on serpentine.Ecology[J],1999,80(1):70-80
    [120]Kunin,W.E.Biodiversity at the edge:a test of the importance of spatial "mass effects" in the Rothamsted Park Grasse xperiments.Proc.Natl.Acal.Sci.U. S.A[J],1998,95(1):207~212
    
    [121] Lindgren PMF,Sullivan TP.Influence of alternative vegetation management treatments on conifer plantation attributes: abundance,species diversity and structural diversity.For Ecol & Manag[J],2001,142:163~182
    
    [122] Magurran,A.E.Ecological Diversity and its Measurement[M],New Jersey:Princeton University Press, 1998
    
    [123] Marshall E J P. The horizontal movement of seeds in an able soil by different soil cultivation methods[J].Journal of applied ecology,1999,36:443~453
    
    [124] Pitkanen S.Effects of tree stand and site variables on alpha diversity of ground vegetation in the forests of Northern Karelia. Environ Manag [J],2000,58:289~295
    
    [125] Raunkiaer C. The Life-form of Plant and Statistical Plant Geography[M]. Oxford: Clarendon Press, 1934
    
    [126] Simpson R L. Seed bank of a freshwater tidal wetland: turn over and relationship to vegetation change[J] .American journal of botany, 1987,74:3 60 ~ 3 70
    
    [127] Simpson R L. Tidal freshwater wetland zonation: seed and seeding dynamics[J].Aquatic bitany,1994,47:61~75
    
    [128] Tilman,D.Productivity and sustainability influenced by biodiversity in grassland ecosystems.Nature[J], 1996,379(22):718—720
    
    [129] Tilman,D.The ecological consequences of changes inBiodiversity:A search for general principles.coIogy[J],1999,80(5):1455~1474

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