黄土边坡喷播及植物群落特征和害虫防治研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
研究边坡绿化与防护既是国家的重大技术需求,又具有较大的理论意义和实用价值。为此,于2007年至2010年在评定高速公路的甘肃平凉段,采用L_4(2~3)的正交试验设计,用第三年的地上生物量为考察指标,建成了4个人工植物群落,并以此作为研究各群落特征、群落发育、群落物种多样性和害虫防治技术的对象,取得了以下主要结论。
     (1)对试验因子分析结果证明各因子的重要性顺序是:喷播建植技术>草种组合>肥料种类。比较同一因子的不同水平发现:客土喷播是主要因子,其次是草种组合。变量分析表明:试验重复间差异不显著,试验因子间差异均达到0.05显著水平。
     通过试验建成了4个与试验处理相对应的人工植物群落:群落Ⅰ—紫羊茅+草地早熟禾+异穗苔草-胡枝子群落;群落Ⅱ—赖草+白颖苔草-铁杆蒿+莳萝蒿群落;群落Ⅲ—紫花苜蓿+异穗苔草+灰绿藜铁-铁杆蒿群落;群落Ⅳ—高羊茅+早熟禾+白颖苔草+匍茎剪股颖群落。
     (2)各人工群落的主要特征是:均以禾本科、菊科和豆科植物占绝对优势;种类组成差异很大;喷播草种性质分化程度大;各群落的最小面积排序是群落Ⅱ>群落Ⅲ>群落Ⅳ>群落Ⅰ;群落间科、属、种的最大共同度出现在群落Ⅱ、Ⅲ比对中,最小共同度出现在群落Ⅰ、Ⅱ比对中,草本植物层、禾本科植物和菊科植物种的最大共同度均出现在群落Ⅱ、Ⅲ比对中;相对频度级的大小顺序是群落Ⅱ>Ⅲ>Ⅰ>Ⅳ;地上芽、地面芽和地下芽是各群落结构的基本层片,其中,群落Ⅱ、Ⅲ的地面芽和地下芽植物尤为发育。
     人工植物群落特征表明:群落的科、属、种数与试验处理有关;客土喷播的植物群落种类组成相对复杂,喷播草种的优势度、竞争力及生态学意义逐渐被当地地带性或区域性植被的优势种所取代,但群落发育仍然处在初级阶段;群落的种类数越多,群落的最小面积相应地就越大;群落Ⅱ、Ⅲ的种类组成和生境条件相似性程度高,而群落Ⅰ、Ⅱ的相似性程度低;多年生丛生禾草、莎草和多年生蒿属小半灌木植物是各群落的优势类群;在黄土边坡建立的防护植物群落,其发育过程与当地撂荒地和退耕还草地植被恢复过程相似,预示着植物生存环境逐渐良性化,喷播草种具有先锋植物和促进次生植被恢复的功能。
     (3)研究人工植物群落发育表明:湿性喷播的群落Ⅰ和群落Ⅳ中,喷播的草种在平均密度、平均频度、平均盖度和种的重要值方面都占优势,显示出它们在群落内的重要性,图解显示群落Ⅳ比群落Ⅰ发育较良好;在客土喷播的群落Ⅱ和群落Ⅲ中,优势度最大的10种植物在平均密度、平均频度、平均盖度和种的重要值方面都占优势,图解显示,群落Ⅲ比群落Ⅱ的各项指标配置合理;从群落功能讲,群落Ⅱ和群落Ⅲ的护坡效果都比较好。
     (4)黄土边坡4个人工植物群落种的丰富度和α多样性指数自大至小排序是:群落Ⅱ>群落Ⅲ>群落Ⅳ>群落Ⅰ。种的均匀度指数排序是:群落Ⅰ>群落Ⅳ>群落Ⅲ>群落Ⅱ。排序规律比较好地反映出了各群落的组织化水平、护坡功能、动态及群落的稳定性特点。
     (5)群落内主要植物层片和优势类群种的丰富度、均匀度与α多样性分析结果证明:草本植物层和禾本科植物分别在各群落中具有重要作用,但年轻的群落还没有足够的时间达到种类多样化的程度,随着时间的推移,其种数将会越来越多样化。
     (6)各群落间种的相异性与β多样性分析结果:在4个群落的6个比对中,Cody指数自大至小的排序是Ⅰ-Ⅱ>Ⅲ-Ⅳ>Ⅰ-Ⅳ>Ⅱ-Ⅳ>Ⅰ-Ⅲ>Ⅱ-Ⅲ;各群落相似性程度的顺序是Ⅱ-Ⅲ>Ⅱ-Ⅳ>Ⅰ-Ⅲ>Ⅲ-Ⅳ>Ⅰ-Ⅱ;进一步分析了各群落间主要植物层及优势类群种的相异性与β多样性。种的相异性与β多样性分析结果比较好地显示了群落间及群落间主要层片和优势类群物种取代程度与生境的差异性。
     (7) 2009年夏秋之间调查黄土边坡护坡植物群落中的害虫,采集标本7025只,分隶于8目、22科、35属、39种,其中夜蛾科的粘虫是优势种害虫。
     (8)将黄土边坡护坡植物群落中的害虫混合种群划分成5个密度梯度,用同一剂量(53.55ml/1000m~2)的4.5%氯氰菊酯EC进行防治试验发现:防效与虫口密度之间具有较高的正相关关系(r= 0.9771);最高防效只有62.84%,表明53.55ml/1000m~2的有效剂量偏低。
     (9)用等比系列用药量对害虫混合种群进行防治试验发现:防效还与4.5%氯氰菊酯EC的使用浓度密切相关(r = 0.9754)。
     (10)根据试验结果,用机率值法进行测算,4.5%氯氰菊酯EC对害虫混合种群的毒力可用y = 2.2476 + 5.1118 x的回归方程表示,并据此提出了不同防治效果适宜用药量的模拟结果。
The research on slope greening is the key national technical demand and important for theoretical and practical development. In this case, four plant communities were established in Pingliang from 2007 to 2010 to study the features, development, species diversity and pest control of community with orthogonal experimental design by measuring the biomass. The main results are as follows:
     1. The importance order of affecting factors was spay seeding technique > grass species composition > fertilizers. The guest soil was the main factor and followed by the grass species composition while the same factor was compared. And the difference among treating factors was significant at 0.05 level.
     Four plant communities were established including CⅠ( Festuca rubra + Poa annua + Carex heterostachya -Leapedeza bicolor) , CⅡ( Leymus secalinus + Carex rigescens-Ajiania gmalinii + Ajiania anethoides), CⅢ(Medicago sativa + Carex heterostachya + Chenopodium glaucum - Ajiania gmalinii) and CⅣ(Festuca arundinacea + Poa angustifolia + Carex rigescens + Agrostis stolonifera).
     2. The main characteristics of established communities could be described as follows: The dominants were gramineous, feverfew and legumes and the species composition greatly varied. The performance of spray seeding grass species was greatly different. The order of least area ranking of four communities was CⅡ> CⅢ> CⅣ> CⅠ. The maximum communality of family, genus and species among communities occurred between CⅡand CⅢ. And the minimum communality occurred between CⅠand CⅡ. The maximum communality of grass synusia, gramineous and feverfew occurred between CⅡand CⅢ. The order of relative frequency was CⅡ> CⅢ> CⅠ> CⅣ. The chamaephyte, hemicryptophyte and geophyte were the main component of each synusia, in which, the hemicryptophyte and geophyte were dominant in CⅡand CⅢ.
     The result indicated that the species number of community was related to the experiment treatments. The species composition of communities establish through spay seeding was relatively complex. Although the community was at the early development stage, the plant species were gradually replaced by native species. The more species number, the greater least area. The similarity of plant composition and habitat between CⅡa nd CⅢwas high and it was low between CⅠa nd CⅡ. The bunch grass, sedge and perennial subshrub were the dominants in each community. The development of community established through spray seeding was similar with the community in recovering abandoned arable land, it means that the habitat was in restoring period and the plant in spray seeded community played the pioneer role.
     3. The average density, frequency and coverage of grasses in wet spray seeded communities (CⅠand CⅣ) were high and it indicated their importance, and CⅣdeveloped batter than CⅠ. As for the guest soil spray seeded communities (CⅡand CⅢ), 10 plant species performed batter and CⅢwas better than CⅡ. In terms of community function, the slope protection effect of CⅡⅣand CⅢwas satisfied.
     4. The order of richness andαindex of 4 communities was CⅡ>CⅢ>CⅣ>CⅠ. The order of evenness index was CⅠ>CⅣ>CⅢ>CⅡ. This ranking pattern reflected the organizing level, slope protection effect and community stable ability.
     5. The analysis on richness, evenness andαindex of main synusia indicated that grass synusia and gramineous species played an important role in communities. However, the diversity of young community was not high because of developing time and it would be more diverse in future.
     6. The dissimilarity among communities andβindex analysis indicated that the order of Cody index among 4 communities wasⅠ-Ⅱ>Ⅲ-Ⅳ>Ⅰ-Ⅳ>Ⅱ-Ⅳ>Ⅰ-Ⅲ>Ⅱ-Ⅲ. And the order of similarity among communities wasⅡ-Ⅲ>Ⅱ-Ⅳ>Ⅰ-Ⅲ>Ⅲ-Ⅳ>Ⅰ-Ⅱ. The analysis on dissimilarity of species composition andβindex could explore the replacing degree and habitat difference among synusia and communities.
     7. Totally 7025 pest specimen, belonging 8 subject, 22 family, 35 genus and 39 species. In which, the armyworm in cutworm family was the dominant pest.
     8. The pest in slope protection community could be divided into 5 density gradients. The relationship between control efficiency and peat density was positive (r=0.9771) by using same dose of 4.5% cypermethrin EC (53.55 ml/1000m~2). The highest control efficiency was only 62.84%, which means that the dose was low.
     9. The result of control experiments with different doses indicated that the control efficiency was also related to the concentration of cypermethrin EC (r=0.9754).
     10. The virulence of 4.5% cypermethrin EC to mixed pest population could be described as y = 2.2476 + 5.1118 x, and the suitable concentration could be simulated according to this model.
引文
[1]方华.植被护坡现状与展望[J].水土保持研究,2004,11(3):21-232.
    [2]王卓娟,王世梅.边坡出之中的绿化技术综述[J].贵州水力发电,2007,21(1):53-57.
    [3]李立新,张立军,徐明.高等级公路边坡植物防护与绿化技术综述[J].2005,(4):6-7.
    [4]许涤平.高速公路绿化边坡防护技术[J].资源与环境,2007,25.
    [5]白史且.高速公路绿化工程技术[M].中国农业出版社,2001:56-59.
    [6] Mukaiyama S.Degradation of grassland in Keerqin sandland ,Inner Mongolia,China[J]. Grassl and Science,1998,44:109-114.
    [7] Wang Yun-bing,XU Xiao-wa,MA Xin-ling,WANGGJin-wei,YUHao.MAJORLAWN DISEAES , PES AND WEEDS INHENAN PROVINCE[J].Chinese journai ofGrassland 2006,,28(4):49-52.
    [8]杨兵,李武强.城南高速公路路堑边坡生态防护工程的施工及质量检验标准[J].公路交通技术,2004,(1):64-97.
    [9]刘向东.秦沈客运专线路基边坡植被防护工程设计与施工[J].铁路工程学报,2002,73(1):86-88.
    [10] Embassy US.Grassland Degradation in Tibetall Regions of China:Possible Recovery Strategies[R].Network:Global Business Development,1996.385-417
    [11] Liu X,Chen B. Climatic warming in the Tibetan Plateau during recent decades[J]. Int.J.Climatol1,2000,20(14): 72-74.
    [12] Sthind M S,Dhillon.Degraded lands of panjab and their development through agro forestry. In: Agroforestry System for Degraded Lands. Oxford IBH Publishing Co. Pve Ltd .1994,(1):13-12.
    [13] Gray D Hsotir B. Biotechnical stabilization of steepened slopes[A].In: Paper Present at the Transportation Research Board of the 746th Annual meeting[C].[s.n],1995.1-5.
    [14] Gray D Hsotir B. Biotechnical stabilization and Soil Bioengineering Slope Stabilization-a Practical Guide for Erosion Control[M]. New York: John Wiley and Sons ,Inc,1996.6-8.
    [15] Lin H D,Kung J H S . Rainfall-induced slope failure in Taiwan[A].In:Asian Conf. on Unsaturated Soils from Theory to Practice[C].[s.1]:[s.n],2008.801-806.
    [16]冯正一,林永光.考量环境、生态与景观需求之边坡保护技术[J].地工技术,1991,92:61-70.
    [17]张政,付融冰.河道坡岸生态修复的土壤生物工程应用[J].湖泊科学,2007,19(5):558-565.
    [18]关丽杰,陶飞,刘宁.北方地区常见草坪品种对二氧化氮的抗性研究[J].辽宁化工,2005,34(5):206-208.
    [19] LiY H.Impact of grazing on Aneurolepidium chinensis steppe and Stipagran dissteppe[J].Acta Oecologica,1989,10:31-46.
    [20] Carroll C,Merton L,Burger P. Impact of vegetation cover and slope on runoff, erosion, and water quality for field plots on a range of soil and spoil materials on central Queenlands coal mines[J]. Aust. J. Soil Res.,2000,38:313-327
    [21]赵宝军.挂网客土喷播技术在高速公路边坡防护中的作用[J].山西交通科技,2004,164(4):20-22.
    [22]梁云波,孙强,李海滨.岩石边坡绿化的有效方法—厚层基质挂网喷播法[J].现代农业科技,2006,31-32.
    [23]关大力,蔡树龙.高等级公路的边坡稳定与防护[J].黑龙江交通科技,2006,148(6):19-20
    [24]查轩,唐克丽,张科利,等.植被对土壤特性及土壤侵蚀的影响研究[J].水土保持学报, 1992, 6 (2):52-59.
    [25]梁爱学,刘国栋,李强,等.三维网边坡防护技术研究[J].公路交通科技,2005,5:15-18
    [26]郭庆淀,顾跃强,张立杰.高强土工格室在高速公路路基施工中的应用[J].山西建筑,2009,35(4):298-300.
    [27]金建红,叶圣绿,金家国.客土喷播技术在公路边坡生态恢复中的应用[J].山西建筑,2008,34(21):343-344.
    [28]罗剑.客土喷播植草施工简介[J].山西建筑2007,33(25):297-298.
    [29]郑海金,曾峰海,欧立业.粉煤灰对土壤性质和草坪生长的影响[J].土壤,2005,37(2):205-209.
    [30]袁菊,刘方,张卫兵,罗海波.粉煤灰基质上草坪草苗期生长状况及其评价[J].生态学杂志,2005,24(5):493-496.
    [31]王大力,尹澄清.植物根孔在土壤生态系统中的功能[J].生态学报,2000,20(5):869-874.
    [32]赵宇.我国园林植物的生态效应研究现状[J].北方园艺,2006,01期22-23.
    [33]王蕾,王志,刘连友,哈斯.城市园林植物生态功能及其评价与优化研究进展[J].环境污染与防治,2006,(01)31-34.
    [34]苏翔,杜娟,曹映泓,等.生态工程在高速公路岩石边坡防护工程中的应用[J].公路2001,(7)86-89.
    [35]蒋鹏飞,舒安平,沈小明,杜娟.客土喷播在临长高速公路石质边坡防护中的应用[J].湖南交通科技,2002,28(4):68-69.
    [36]李虹.厚层基材喷播法在昌泰高速公路石质边坡率绿化中的应用[J].公路环境保护,2004,(3):88-90.
    [37]陈晓斌.客土喷播法在石质边坡绿化中的应用[J].公路,2004,(8):307-309.
    [38]马万全,沈康健,邓辅唐.客土喷播技术对石质边坡防护的应用[J].云南交通科技,2003,19(3):74-79.
    [39]陈向阳.石质边坡绿化在漳龙高速公路上的应用[J].公路,2002,(1):247-249.
    [40]段湘龙,钟国安.边坡防护的新技术[J].黑龙江交通科技,2006,9(151):23-24
    [41]周庆桐,译.坡面绿化施工法[M].北京:人民交通出版社,1988,2:98-101.
    [42]罗晶,等译.恢复自然环境绿化工程概论——坡面绿化基础与模式设计[M].北京:中国科学技术出版社,1997,125-128.
    [43]涂序流,奚如春,邓小梅.赣粤高等级公路护坡草坪建植技术—以泰(和)赣(州)工程段为例[J].江西林业科技2005,(2):32-34.
    [44]成子桥.客土喷薄技术在泌桐高速公路的应用[J].隧道建设,2007,27(1):80-83.
    [45]李群善,邹胜文.西部地区公路生态环境建设[J].公路,2001,(6):87-91
    [46]安保昭.坡面绿化法[M].北京:人民出版社,1988.17-41.
    [47]王大庆.黑龙江省公路路堑边坡防护工程滑塌病害的成因与防治[J].黑龙江交通科技,2006,145(3):16-19.
    [48]卢敦华,王星华.植被根系系统加固破碎岩坡的作用机理[J].科技导报,2007,245(23):
    [49]李鹏,李占斌,张兴昌.草灌植被拦蓄径流和泥沙有效性研究[J].水土保持学报,2002, 16 (1):32-34.
    [50]王秋生.植被控制土壤侵蚀的数学模型及其应用[J].水土保持学报,1991,5 (4):68-72.
    [51]肖盛燮,周辉,凌天清.边坡防护工程中植物根系的加固机制与能力分析[J].岩土力学与工程学报,2006,25(2):51-54.
    [52]周跃,徐强,络华松,等.乔木侧根对土体的斜向牵引效应(I原理和计算模型)[J].山地学报,1999,17(1):10-15.
    [53]吕春春.浅谈太原—长治高速公路的边坡防护[J].2005,176(2):14-15.
    [54]王刚.浅谈沈本高速公路路堑边坡治理及防护[J].辽宁交通科技,2003,(4):27-28.
    [55]王金发,王晓明.高速公路边坡绿化防护[J].2003,111(5):38-40.
    [56]周跃,徐强,络华松,等.乔木侧根对土体的斜向牵引效应(I原理和计算模型)[J].山地学报, 1999,17(1):4-9.
    [57]张俊云,周德培,李绍才.岩石边坡生态护坡研究简介[J].水土保持通报,2000,20(4):36-38.
    [58]王可钧,李焯芬.植被固坡的力学分析[J].岩土力学与工程学报,1998,17(6): 687-691.
    [59]孙祥柱,曾宪毅.高等级公路的边坡防护[J].黑龙江交通科技,2007(4):45.
    [60]吴东强,罗幸平.高等级公路边坡绿化防护方法[J].公路与汽运,2001,(85):27-29.
    [61]曾田,王莉.公路边坡综合防护技术[J].黑龙江交通科技,2006,147(5):19-21.
    [62]康金花,郝丽.硫酸除氯在含氯土壤有机质测定中的应用[J].干旱区研究,2004,21(1):67-71.
    [63]张华君,吴曙光.边坡生态防护方法和植物的选择[J].公路交通技术,2004,4(2):37-39.
    [64]施发正.草坪的应用与自然式草坪的植物配置[J].现代农业科技,2006,56.
    [65]陈利军,刘高焕,励惠国.中国植被净第一性生产力遥感动态监测[J].遥感学报,2002,6(2):129-135.
    [66]汪诗平,李永宏,王艳芬,韩苑鸿.不同放牧率下冷蒿小禾草草原放牧演替规律与数量分析[J].草地学报,1998,(04):299-305.
    [67]高凯,刘自学,胡自治,等.不同草种单播草坪蒸散量的研究[J].草原与草坪,2004,105(2):43-46.
    [68]谢莉萍,徐世杰.公路边坡稳定与防护问题[J].黑龙江交通科技,2005133(3):29-32.
    [69] W arm ing, -E.植物生态学植物群落研究引论(陈庆诚译) [M].北京:科学出版社, 1965. 4-7.
    [70] Gam s,H. Prinzipiebfragen der Vegetations for schung [J]. V jschr. N aturf. Ges. Zur ich,1918,63: 293- 493.
    [71] Rexford D aubenm ire.植物群落生态学教程(陈庆诚) [M].北京:人民教育出版社,1981.1-9.
    [72]阿略兴B. B.植物地理学(傅子祯等译)[M].北京:高等教育出版社,1957. 15-27.
    [73]林鹏.植物群落学[M].上海:上海科学技术出版社,1986. 1213.
    [74]孙儒泳,李博,诸葛阳,等.普通生态学[M].北京:高等教育出版社,1993. 147.
    [75]李日红.植物群落的特点和演替[J].中山大学学报论丛,2000,20(5):27-31.
    [76]左大康.现代地理学辞典[M].北京:商务出版社,1990.856-857.
    [77] Curr ie D J. Energy and large- scale patterns of anim al and plant- species richness[ J]. Am erican N aturalis,t 1991,137: 27-49. [78 ] Lev in S A. Fragile dom in ion R eading [M].M assachusetts: H e lix Books,1999.70- 72.
    [79]陈昌笃,李迪华.湖南省武陵源地区的生物多样性和生态完整性[J].生态学报,2003,23(1):2414- 2423.
    [80]刘会玉,林振山,张明阳.人类周期性活动对物种多样性影响及其预测[J].生态学报,2005,25(7):1633-1640.
    [81]郑成洋,刘增力,方精云.福建黄岗山南坡和西北坡乔木物种。多样性及群落特征德垂直变化[J].生物多样性,2004,12(1):63~74.
    [82] K essler,M. Elevationa lgradients in species richness and endem ism of selected plant groups in the centra l Bo liv ian Andes[J]. Plant Ecology,2000,149:181- 193.
    [83] Lom olino,M. V. E levation gradients of species- density:histori cal and perspective views [J]. G lobal Eco logy and B iogeogra phy,2001,10:3-13.
    [84]刘振国,李镇清,董明.植物群落动态模型分析[J].生物多样性,2005,13(3): 269-277.
    [85] M iles J. V egetation Dynam ics[M ]. New York:H a lsted Press,1979. 1- 206.
    [86] P ickett ST A. S L Collins,J JA rm esto. M odels,m echanism s and pathways o f succession [J]. The BotanicalR eview,1987,53:335- 371.
    [87] Crim e J P. P lant Strategies and V egetation P rocesses [M]. W I ley,Chichester,U. K.,1979. 1-280.
    [88]杨志焕,葛滢,沈琪,等.亚热带人工湿地中配置植物与迁入植物多样性的季节变化[J].生物多样性,2005,13( 6): 527 534.
    [89]王仁忠,晓强,马克平.中国植物生态学研究进展%.近十年来中国植物种群生态学研究[J].植物学报,2003,45(增刊):64~69.
    [90]米湘成,马克平.中国植物生态学研究进展:中国植物群落生态学研究[J].植物学报, 2003,45(增刊):70~76.
    [91]魏伟.中国植物生态学研究进展:中国植物分子生态学10年进展[J].植物学报,2003, 5(增刊):77~ 84.
    [92]彭少麟.南亚热带森林群林群落动态学[M].北京:科学出版社,1996.185
    [93] PICKETT S T A ,WHITE P S.The ecology of natural disturbanceand patch dynamics [M].New York:Academic Press.11985,1341.
    [94] McINTOSH R P.The background of ecology [M].Cambridge:Cam-bridge University Press ,1985, 654.
    [95] Clements F E.plant succession:An analysis of the development ofvegetation [M]Publication No.242.Carnegie Institution of Washing-ton.1961.722-731.
    [96]刘建国.当代生态学博论[M].北京:中国科学技术出版社,1992,215-221.
    [97] Tilman D.The resource -ratio hypothesis of plant succession [J]American Naturalist,1985,125:827- 852.
    [98] Pickett S T A.A hierarchical consideration of causes and mech-anism of succession[J].Vegetation,1987,69:109- 114.
    [99]范竹华,法永乐,李梅,等.生态演替螺旋式上升理论探析[J].农业与技术.2005,25(1):99-101.
    [100] Knap.植被动态[M].李博译.北京:科学出版社,1985. 176-180.
    [101]马克平,刘玉明.生物群落多样性的测度方法α多样性的测度方法(下)[J].生物多样性,1994,2(4):231-239.
    [102]贺金生等.长江三峡地区退化生态系统植物群落物种多样性特征[J ].生态学报,1998,18 (4):399 - 407.
    [103]贺金生等.中国中亚热带东部常绿阔叶林主要类型的群落多样性特征[J].植物生态学报,1998,22(4):303 - 311.
    [104]黄忠良等.鼎湖山植物物种多样性动态[J].生物多样性,1998,6(2):116 - 121.
    [105]彭少麟等.鼎湖山厚壳桂群落演替过程的组成和结构动态[J].植物生态学报,1998,22 (3):245 - 249.
    [106]王峥峰等.海南岛吊罗山山地雨林物种多样性[J].生态学报,1999,19(1):61 - 67.
    [107]丁圣彦,宋永昌.浙江天童国家森林公园常绿阔叶林演替前期的群落生态学特征[J].植物生态学报,1999,23(2):97 - 107.
    [108]马克平等.北京东灵山地区植物群落多样性研究Ⅷ.群落组成随海拔梯度的变化[J].生态学报,1997,17(6):593 - 600.
    [109]石培礼等.四川卧龙高山林线生态交错带群落的种2多度关系[J].生态学报,2000,20 (3):384 - 389.
    [110] Stohlgren,T. J. et al. Comparison of range - land vegetationsampling techniques in t he Cent ral Grasslands [J] .J. R ange M anage,1998,51(2):164 - 172.
    [111]彭少麟等.广东森林群落的组成结构数量特征[J].植物生态学与地植物学学报,1989,13(1):10 - 17.
    [112]刘灿然等.北京东灵山地区植物群落多样性的研究样本大小对多样性测定的影响[J].生态学报,1997,17 ( 6):584 -592.
    [113] Magurran,A. E. Ecological Diversity and it s Measurement[M]. New J ersey:Princeton University Press,1998.456-462.
    [114]马克平,等.北京东灵山地区植物群落多样性研究——丰富度、均匀度和物种多样性指数[J].生态学报,1995,15 ( 3):268 -277.
    [115]高贤明,陈灵芝.北京山区辽东栎( Q uercus liaot u ngensis)群落物种多样性的研究[J].植物生态学,1998,22(1):23 - 32.
    [116] Hart nett,D. C. and Wilson,W. T. Mycorrhizae influence plant community st ruct ure and Diversity in tallgrass prairie [J]. Ecology,1999,80(4):1187 - 1195.
    [117]温远光等.大明山中山植被恢复过程植物物种多样性的变化[J].植物生态学报,1998,22 (1):33 - 40.
    [118]岳明.秦岭及陕北黄土区辽东栎林群落物种多样性特征[J] .西北植物学报,1998,18(1):124 - 131.
    [119]黄建辉,等.地带性森林群落物种多样性的比较研究[J].生态学报,1997,17(6):611-618.
    [120]马克平.生物群落多样性的测度方法α多样性的测度方法(上) [J].生物多样性,1994,2(3):162- 168.
    [121]潘开文.岷江上游暗针叶林采伐迹地人工混交林群落结构[J].武汉植物学研究,1999,17(2):130 - 136.
    [122]黄忠良,等.鼎湖山植物群落多样性的研究[J].生态学报,2000,20(2):193 - 198.
    [123]马克平等.北京东灵山地区植物群落多样性研究Ⅲ.几种类型森林群落的种-多度关系研究[J].生态学报,1997,17 ( 6):573 - 583.
    [124]谢晋阳,陈灵芝.中国暖温带若干灌丛群落多样性问题的研究[J].植物生态学报,1997,21 (3):197 - 207.
    [125]郑元润.大青沟森林植物群落物种多样性研究[J].生物多样性,1998,6(3):191 - 196.
    [126]奚为民.雾灵山国家自然保护区森林群落物种多样性研究[J].生物多样性,1997,5 (2):121 - 125.
    [127]陈北光等.广东大东山常绿阔叶林物种多样性分析[J].华南农业大学学报,1997 ,18(4):59 - 63.
    [128]叶万辉.物种多样性与植物群落的维持机制[J].生物多样性,2000,8(1):17 - 24.
    [129]庄树宏,等.昆嵛山老杨坟阳坡与阴坡半天然植被植物群落生态学特征的初步研究[J].植物生态学报,1999,23 ( 3):238 -249.
    [130] Tilman D,Pacala S. The Maintenance of species richness in plant communities [A].In : Richlefs,R. E. ( eds. ). SpeciesDiversity in Ecological Communities [C] Chicago: The University of Chicago Press,1993,13 - 25.
    [131]贺金生,陈伟烈.陆地植物群落物种多样性的梯度变化特征[J].生态学报,1997,17 (1):91 - 99.
    [132] Reynolds,H. L. Soil heterogeneity and plant competition in an annual. grassland[J] Ecology,1997,78 (7):2076 - 2090.
    [133] Tilman,D. Competition and biodiversity in spatially st ruct ured habitat s[J].Ecology, 1994,75 (1):2 - 16.
    [134]贺金生等.中国中亚热带东部常绿阔叶林主要类型的群落多样性特征[J].植物生态学报,1998,22(4):303 - 311.
    [135] Harrison,S. Local and regional diversity in a partly landscape:native, alien and endemic herbs on serpentine [J].Ecology,1999,80 (1):70 - 80.
    [136]贺金生,马克平.物种多样性[A].见:蒋志刚.保护生物学[C].杭州:杭州科学技术出版社,1997.20-33.
    [137]李新荣等.我国干旱沙漠地区人工植被与环境演变过程中植物多样性的研究[J].植物生态学,2000,24(3):257 - 261.
    [138] Tilman,D. et al. Productivity and sustainability influenced by biodiversity in grassland ecosystems [J].Nature,1996,379 (22):718 - 720.
    [139]马克明,等.北京东灵山地区森林的物种多样性和景观格局多样性研究[J].生态学报,1999,19(1):1 - 7.
    [140] Elton,C. S. The reasons for conservation[A]. In:The Ecology of Invasions by Animals and Plant s [M]. London:Chapman &Hall,1958,143 - 153.
    [141] Tilman,D. and Dowing,J. A. Biodiversity and stability in grasslands[J]. N at u re,1994,367:363 - 365.
    [142] Baskin,Y. Ecosystem function of biodiversity [J].B io. Science,1995,44:657 - 660.
    [143]孙德宙,等.江西大茅山常绿阔叶次生林与人工林生物多样性分析[J].林业科学研究,1998,11(4):402 - 406.
    [144] Ewel.J. J .et al.Tropical soil fertility changes under monocult ures and successional communities of different st ruct ure [J] .Ecol . A ppl.,1991,1:289 - 302.
    [145] Givnish,T. L. Does diversity beget stability[J] ? N at u re,1994,37(8):113 - 114.
    [146]李振基,等.武夷山自然保护区郁闭稳定甜槠林与人为干扰甜槠林物种多样性比较[J].植物生态学报,2000,24 (1):64 -68.
    [147] McNaughton,S. J. Biodiversity and function of grazing ecosystems in Biodiversity and ecosystem function [ A ] .In :Schulze,E. D. ( eds. ). Ecological St udies [C].New York:Springer - Verlag,1993,99:361 - 383.
    [148]李新荣,ПавловБН.俄罗斯平原针阔林过渡带森林群落组成结构与物种多样性的研究[J] .生物多样性,1999 ,7 ( 4) :291 - 296.
    [149] Pimm,S. L. The complexity and stability for ecosystems[J]. N at u re ,1984 , 307 (26):321 - 326.
    [150] Kunin,W.E.Biodiversity at t he edge:a test of t he importance of spatial“mass effect s”in t he Rot hamsted Park Grassexperiment s[J].Proc. Natl. Acal. Sci. U. S. A. 1998,95(1):207-212.
    [151] Collins,S.L. et al. Experimental Analysis of Intermediate dist urbance and initial floristic composition:decoupling cause and effect [J ] .Ecology,1995,76(2):486 - 492.
    [152]黄建辉.物种多样性的空间格局及其形成机制初探[J].生物多样性,1994,2(2):103-107.
    [153] Ehrlich,P. R. and Ehrlich A. H. Extinction. The Causes and Consequences of t he Disappearance of Species [ M ] . Random House , 1981.
    [154] Walker B. Biodiversity and ecological redundancy[J].Conserv. Biol.,1992,6 :18 - 23.
    [155] Tilman,D.The ecological consequences of changes inBiodiversity:Asearch for general principles[J].Ecology,1999,80(5):1455-1474.
    [156]马范,石隐孝,向得福,成若琳,等.甘肃草地资源[M].兰州:甘肃科技出版社,1999.26-65
    [157]丁连生,李善堂,赵忠,刘荣堂,等.甘肃草业可持续发展战略研究[M].北京:科学出版社,2008,288-352.
    [158]荣廷昭.田间试验与统计分析[M].北京:中国农业出版社,1998,92-95,250-260.
    [159]郑铁琦,王志勇,郭海林,薛丹丹,刘建秀.正交设计优化假俭草SRAP-PCR反应体系及引物筛选[J].草业学报,2008,(4):110-117.
    [160]云南大学生物系.植物生态学[M].北京:人名教育出版社,1980,185-264.
    [161]王伟杰.秦岭北坡南五台地区主要森林植物群落的结构和生态特征的初步研究[J].植物生态学与地植物学丛刊,1965,287-306.
    [162]马克平.生物多样性的测度方法Ⅰα多样性的测度方法(上)[J].生物多样性,1994,2(3):162-168.
    [163]马克平.生物多样性的测度方法Ⅰα多样性的测度方法(下)[J].生物多样性,1994,2(4):231-239.
    [164]马克平.生物多样性的测度方法Ⅱβ多样性的测度方法(上)[J].生物多样性,1995,3(1):38-43.
    [165]韩丽娟,顾中言,王强,黄祥麟,许小龙.农药复配与复配农药[M].南京:江苏科学技术出版社,1994,31-39.
    [166]陈扬林,陈万权,谢水仙,张淑香,等.粉秀宁药效与小麦品种对条锈菌感病性关系的研究[J].植物保护学报,1992,19(1):75-79.

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700