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晋西黄土区林草植被特征数量化研究
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摘要
本文研究区为山西吉县蔡家川流域,通过外业调查和内业数据分析,较为系统的研究了该区乔、灌、草各层植被的数量特征。文章从研究林木直径、树高结构来探讨乔木层的植被特征,从生物多样性在不同地形因子下的变化规律来研究灌、草层的结构特征,并对灌草层物种、样方、环境因子进行排序,研究结果以期为晋西黄土区林分的可持续经营、植被恢复与重建过程中林草种的配置、低效林的改造提供理论依据。
     本文研究的主要结论如下:
     (1)不同地形因子对林木胸径、树高分布的影响分析。
     1)阴坡胸径值相对集中于0.5cm~8.5cm,在2.5cm~3.5cm范围胸径分布值最大;阳坡胸径值相对集中在0.5cm~15.5cm范围内,在5.5cm~6.5cm区间内胸径值最多。从阴坡、阳坡总体情况看,树高分布相对集中,在3.75m~4.25m之间树高值均最多。
     2)该区的缓坡和急坡地带胸径分布比较分散,胸径值不超过22cm,在斜坡和陡坡地带胸径分布相对集中在0.5cm~16cm的范围内;在缓坡和急坡树高零星分布,偶有集中,在斜坡和陡坡树高分布集中度好,树高多分布在0.45m~8m范围内。
     3)不同海拔林木胸径、树高分布。在1100m~1200m海拔高度胸径分布集中度非常明显,在此海拔内的胸径分布值大部分在0.5cm~16cm范围内。在1000m~1100m海拔高度胸径分布相对集中在4cm~13cm范围内,其它海拔高度上胸径分布比较分散与均一;在1100m~1200m之间树高分布集中度明显,多集中于0.45m~8m之间。在1000m~1100m海拔范围内树高分布较集中,在3.6m高度上值最多,其它海拔高度上树高值分散。
     (2)各种立地条件下的林木胸径、树高分布拟合。该区胸径最服从于3参数weibull分布,用三种分布拟合树高效果差。胸径-频率直方图和树高-频率直方图展示了不服从三种分布的胸径、树高分布状况。
     (3)研究区优势灌草种的分布特性分析。虎榛子、多花胡枝子、毛丁香、黄刺玫、铁杆蒿、矮苔草、甘菊能适应该区不同立地环境,胡枝子、连翘、杭子梢、黄栌、野艾蒿、狭叶青蒿、异叶败酱、黄芩、茅莓、南蛇藤均是耐阴喜湿润物种,截叶铁扫帚、白羊草为喜光抗旱物种。
     (4)不同立地条件下研究区灌、草层物种的分布。研究表明林下灌草种较稳定、均匀的分布在各种立地环境下。在阳坡不同坡位上草本种的优势度相差不大,但是随着坡位的下降物种有越来越丰富的趋势,在中坡位时物种均匀性程度稍低。阴坡时不同坡位对物种的均匀度和优势度影响不明显。
     (5)样方、物种、地形因子之间关系直观的展现在二维排序图上。
This paper takes forest and grass vegetation structure as research object in Caijiachuan Watershed of Ji County in shanxi province.Through field investigation and lab analysis to research their Quantitative Characteristics.Tree layer research focus on Diameter Structure and Tree Height Structure , shrub layer and herb layer study on the Species diversity and display the relationship of Species and environment in diagram by DCCA method.The aim of this research is to supply theoretical basis for research district’s stand sustainable management and species configuration of forest and grass in vegetation restoration and reconstruction,for low-benefit forest transformation.The conclusion show as following:
     (1) The analysis of different terrain factor influence in diameter and tree height distribution.
     1)Diameter value fasten on from 0.5cm to 8.5 cm and the value most from 2.5cm to 3.5cm in shady slope,focus from 0.5cm to 11.5cm in sunny slope and the value most from 5.5 cm to 6.5cm.In 3.75 to 4.25 interval has the most tree height value by overall condition of different slope direction.
     2) Diameter is dispersed distribute in gentle slope and steep slope zone and the maximum is 22cm, form 0.5cm to16cm in clivus and abrupt slope.the most of tree height value is distribute from 0.45m to 8m, the value is convergence in clivus and abrupt slope.
     3) Diameter and tree height distribution in different altitude condition.the distribution of diameter centralize from 0.5cm to16cm from 1100m to1200m,form 4cm to 13cm from 1000m to 1100m.the distribution of tree height centralize from 0.45m to 8m from 1100m to1200m.,diameter and tree heigh value is not in a numerical range in other altitude.
     (2) The distribution fitting of diameter and tree height in different site condition.the diameter fitting by three-parameter weibull distribution has good effect,but the tree height fitting’s results is bad. diameter-frequency histogram and tree height-frequency histogram reveal the distribution that is not fit three-parameter weibull distribution and normal distribution and logistic distribution.
     (3) The distribution character of Advantage shrub and grass species the results shows that: Ostryopsis davidiana, Lespedeza floribunda,Syringa tomentella,Rosa xanthina,Artemisia sacrorum,Dendranthema lavandulifolium,Carex humilis Leyss can adapt to different site environmental. Cotinus coggygria,Celastrus orbiculatus,Lespedeza bicolor,Campylotropis macrocarpa,Forsythia suspensa f. suspense,Rubus parvifolius,Artemisia lavandulaefolia,Artemisia dacunculus L are shade tolerance and pleased wetness species.Lespedeza cuneata and Bothriochloa ischcemum are drought resistance and pleased light species.
     (4) The result of research on Species diversity shows that: shrub and grass species is symmetrical and steady distribution in different site condition.
     (5) The relationship of quadrat and species and Terrain factor display intuitive in Two-dimensional ordination diagram of DCCA.
引文
[1] 邓聚龙.灰色预测与决策[M].武汉:华中工学院出版社,1987.
    [2] 段爱国,张建国,童书振,等.杉木人工林林分直径结构动态变化及其密度效应的研究.林业科学研究,2004,17(2):178-184.
    [3] 段爱国,张建国,童书振.6种生长方程在杉木人工林林分直径结构上的应用[J].林业科学研究,2003,16(4):423-429.
    [4] 段爱国.杉木人工林林分直径结构模拟及其动态变化规律的研究[D].北京:中国林业科学研究院,2002.
    [5] 郭丽虹,李荷云.桤木人工林林分胸径与树高的威布尔分布拟合[J].江西林业科技,2000,(2):26-27.
    [6] 郝占庆,赵士洞,陶大立.长白山北坡阔叶红松林草本植物物种多样性及其季节动态.生物多样性,1994,2(3):125-132.
    [7] 贺金生,陈伟烈.陆地植物群落物种多样性的梯度变化特征.生态学报,1997,17(1):91-99.
    [8] 洪楠,候军.MINITAB 统计分析教程.北京:电子工业出版社,2007.
    [9] 惠刚盈,盛炜彤.林分直径结构模型的研究[J].林业科学研究,1995,8(2):127-131.
    [10]雷波,包维楷,刘俊华,等.不同坡向人工油松幼林下地表苔藓植物层片的物种多样性与结构特征.生物多样性,2004,12(4):410-418.
    [11]李 涛 , 尹 林 克 , 严 成 . 塔 里 木 河 中 游 天 然 植 被 的 数 量 分 类 与 排 序 研 究 . 干 旱 区 地理,2003,26(2):173-179.
    [12]李文灿.对Logistic 方程的再认识[J].北京林业大学学报,1990(2):121-127.
    [13]娄安如,刘文华.燕山山脉植物群落的间接梯度分析与数量分类.北京师范大学学报(自然科学版),2001,37(3):391-395.
    [14]娄安如.天山中段山地植被的生态梯度分析及环境解释.植物生态学报,1998,22(4):364 -372.
    [15]吕勇.树木树高曲线模型研究[J].中南林学院学报,1997,17(4):86-89.
    [16]马克平.生物多样性的测度方法Ⅰ α多样性的测度方法(上).生物多样性,2001,23(4): 84-86.
    [17] 马克平.生物多样性的测度方法Ⅰα 多样性的测度方法(下).生物多样性,1994,2(4): 231-239.
    [18]马胜利.灰色模型在林木直径分布规律研究中的应用[J].林业资源管理, 1999(3) :75-78.
    [19]孟宪宇,岳德鹏.利用联立方程测算林分直径分布的初步研究[J].林业资源管理,1995(6): 39-43.
    [20]孟宪宇.测树学(第2版)[M].北京:中国林业出版社,1996.
    [21]米湘成 , 张金屯 , 张峰 , 等 . 山西高原植被与土壤分布格局关系的研究 . 植物生态学报,1999,23(4):336-344.
    [22]米湘成.张金屯,张峰,等.山西高原植被与气候的关系分析及植被数量区划的研究.植物生态学报,1996,20(6):549-5601.
    [23]潘代远,孔令韶,金启宏.新疆呼图壁盐化草甸群落的DCA,CCA及DCCA分析.植物生态学报,1995,19(2):115-127.
    [24]邱扬.张金屯.关帝山八水沟天然植物群落时空梯度的数量分析.应用与环境生物学报,1999,5(2):113-1201.
    [25]邱水文.林木直径分布收获模型综述[J].华东森林经理,1991,5(2):28-32.
    [26]邱扬,张金屯.DCCA排序轴分类及其在关帝山八水沟植物群落生态梯度分析中的应用.生态学报,2000,20(2):199-206.
    [27]邱扬,张金屯.关帝山八水沟天然植物群落时空梯度的数量分析.应用于环境生物学报,1999,5(2):113-120.
    [28]沈泽昊,张新时,金义兴.地形对亚热带山地景观尺度植被格局影响的剃度分析.植物生态学报,2000,24(4):430-435.
    [29]索 安 宁 , 王 兮 之 , 熊 颖 , 等 .DCCA 在 黄 土 高 原 流 域 径 流 环 境 解 释 中 的 应 用 . 地 理 科学,2006,26(2):205-210.
    [30]汤孟平,周国模,施拥军,等.不同地形条件下群落物种多样性与胸高断面积的差异分析.林业科学,2007,43(6):27-31.
    [31]王霞,杨晓晖,张建军,等.西鄂尔多斯高原植被与环境间的关系研究.中国水土保持科学,2007,5(3):84-89.
    [32]吴甘霖,黄敏毅,段仁燕,等.不同强度旅游干扰对黄山松群落物种多样性的影响.生态学报,2006,26(12):3924-3930.
    [33]谢晋阳,陈灵芝.暖温带落叶阔叶林的物种多样性特征.生态学报,1994,14(4):337-344.
    [34]熊莉军 , 郭柯 , 赵长成 , 等 . 四川大巴山巴山水青冈群落的物种多样性特征 . 生物多样性,2007,15(4):400-407.
    [35]杨小波,张桃林,吴庆书.海南琼北地区不同植被类型物种多样性与土壤肥力的关系.生态学报,2002,22(2):190-196.
    [36]张峰.山西关帝山野生植物资源研究.山地研究,1994,12(3):181-1861.
    [37]张金屯.典范指示种分析-一种新的外在分类方法.植物生态学报,1994,18(4):379-3841.
    [38]张金屯.模糊数学及其应用.生态学报,1992,12(4):325-3311.
    [39]张金屯.排序轴分类法及其应用.生态学杂志,1994,13(3):73-751.
    [40]张金屯.植被数量生态学方法.北京:中国科学技术出版社,1995.
    [41]张金屯.植被与环境关系得分析Ⅱ:CCA和DCCA限定排序.山西大学学报(自然科学版),1992,15(3):292-298.
    [42]张金屯.植被与环境关系的分析Ⅰ:DCA排序.山西大学学报(自然科学版),1993,15(3):182-189.
    [43]赵文智,刘志民,常学礼.降雨量下限引种区沙地樟子松幼林种群数高分布偏斜度和不整齐性.应用生态学报,2002,13(1):6-10.
    [44]周彬,官凤英,陈光清.利用变动系数求林分平方平均直径的株数累积百分数.北京林业大学学报,2001,23(4):84-86.
    [45]朱源,康慕谊.排序与广义线性模型与广义可加模型再植物种与环境关系研究中的应用.生态学杂志,2005,24(7):807-811.
    [46]Ball D F. In:The Soils and Landuse of the District aro und Bangor & Beaumaris Her Majesty's Stationery Office.London,1963.
    [47]Borders B E.In:Patterson WD.Projecting stand tables:A comparison of the Weibull diameter distribution method ,a percentile2based projection method,and a basal area growth projection method[J].For Sci,1990,36:413-424.
    [48]Gates D J,Mcmurtrie.R,Borough C J. In:Skewness reversal of distribution of stem diameter in plantations of Pinus radiata[J].Aust ForRes,1983,13:267-270.
    [49]Greig-Smith P. In:Qnantitative Plant Ecology.Blackwell Scientific Publications Oxford,1983.
    [50]Haara A ,Maltamo M,Tokola T.In:The k2nearest2neighbour method for estimating basal2area diameter distribution[J].Scand J For Res,1997(12):200-208.
    [51]Hil1 M O.In:DEC0RANA-A F0RTRAN Program for Detrended Correspondence Analysis andReciprocal Averaging.Ithaca,Cornel1 University,1979a.
    [52]Hill M O.In:Reciproca1 averagingl:An eigenvector method of ordination.Journa1 of Ecology,1973,61:237-249.
    [53]Hill M O.In:TWINSPAN-A F0RTRAN Program for Arranging Multivariate Data in an Ordered TWO-way Table by Classification of the Individuals and Attrtbutes.Ithaca,Corncll Universlty,1979b.
    [54]Kangas A,Maltamo M.In:Calibrating predicted diameter distribution with additional information[J].For Sci,2000,46(3):390-396.
    [55]KemptonRA eta1,.In:A comparison of three measures of diversity.Biometrws.1978,34:25-37.
    [56]Liu CM,ZhangL J,Davis CJ.In:Afinite mixture model for characterizing the diameter distributions of mixed2species forest stands[J].ForSci,2002,48(4):653-661.
    [57]Magurran A E.In:Ecological diversity and its Mea surement New Jersey.Princetoa University Press,1988.
    [58]Maltamo M,Kangas A.In:Methods based on k2nearest neighbor regression in the prediction of basal area diameter distribution[J].Can JFor Res,1998(28:1107-1115.
    [59]Maltamo M.In:Comparing basal2area diameter distributions estimated by tree species and for the entire growing stock in a mixed stand[J].Silva Fenn,1997(31):53-65.
    [60]Pielou E C.Ecological diversity.John Wiley&Sons Inc,1975.
    [61]Ter Braak,C.J.F.&Smilauer,P.2002:CANOCO Reference manual and CanoDraw for Windows User’s guide:Software for Canonical Community Ordination(Version 4.5).Microcomputer Power(Ithaca,NY,USA),500pp.
    [62]Tham A.In:Structure of mixed Picea abies (L.) Karst.and Betula pendula Roth and Betula pubescens Ehrh.stands in south and middle Sweden[J].Scand J For Res ,1988(3):355-370.
    [63]Titterington.In:Mixture distributions(update)[M].Encyclopedia of statistical sciences,1997,399-407.
    [64]Whittaker R H. In:Evolution and measurement of species diversity.Taxo,1972,21:213-251.
    [65]Zeide B.In:Accuracy of equations describing diameter growth[J].Can J For Res,1989 19:1283-1286.

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