Scientia Agricultura Sinica ›› 2013, Vol. 46 ›› Issue (22): 4733-4744.doi: 10.3864/j.issn.0578-1752.2013.22.011

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Dispersal Limitation Versus Environment Filtering in the Assembly of Plant Communities in the Ziwu Mountains

 WANG  Shi-Xiong, GUO  Hua, WANG  Xiao-An, FAN  Wei-Yi   

  1. College of Life Sciences, Shaanxi Normal University, Xi’an 710062
  • Received:2013-04-28 Online:2013-11-15 Published:2013-10-05

Abstract: 【Objective】Improved regional eco-environment is critical to forming ecologically sustainable land-use policies and accelerating agricultural production. Restoring natural vegetation is one of the effective approaches to improve the ecological conditions, and understanding what governs community assembly is the first step, but has been a continuing challenge for ecologists.【Method】In the Ziwu Mountains of the Loess Plateau, how the community assembly is affected by environmental filtering and dispersal limitation was examined by using canonical variation partitioning and Mantel tests, i.e. partition the variation of community composition/dissimilarity distance between environmental and spatial factors/distance. Three species groups (herb layer, shrub layer and tree layer) that differ in traits of likely importance for environmental filtering and dispersal limitation (height and growth form) were analyzed. 【Result】 All forest types were simultaneously governed by environmental control and spatial processes; together, these processes explain 29% to 65% of the species composition variation (P<0.01). However, the effects of these two processes were varied among species groups; shrub layer and tree layer species were dominated by spatial process while there was similar importance between two processes for herb layer. Mantel and partial Mantel tests showed significant correlations between community dissimilarity and environmental dissimilarity/geographical distance (P<0.05). Herb layer showed a high correlation with environmental dissimilarity while shrub and tree layer displayed high correlations with geographical distance. 【Conclusion】 The assembly of plant communities in the Loess Plateau appears to be simultaneously driven by environmental filtering and dispersal limitation. This case study shows the importance of the dispersal limitation in understanding the forests assembly in the Loess Plateau. Consequently, it is important that management planning for restorations of natural vegetations take into account both habitat heterogeneity and geographical differences.

Key words: niche assembly , neutral assembly , community similarity , canonical variation partitioning , Mantel test

[1]程序. 西北黄土高原区农业与生态恶化及恢复重建的关系. 中国农业科学, 2001, 34(1): 84-90.

Cheng X. Relationship between agriculture, ecological deterioration, restoration and reconstruction in Loess Plateau area of Northwest China. Scientia Agricultura Sinica, 2001, 34(1): 84-90. (in Chinese)

[2]信忠保, 许炯心, 郑伟. 气候变化和人类活动对黄土高原植被覆盖变化的影响. 中国科学: D 辑, 2007, 37(11): 1504-1514.

Xin Z B, Xu J X, Zheng W. Response of vegetation cover change to climate change and human activities in Loess Plateau. Science in China: Series D, 2007, 37(11): 1504-1514. (in Chinese)

[3]Zhang J T. Succession analysis of plant communities in abandoned croplands in the eastern Loess Plateau of China. Journal of Arid Environments, 2005, 63(2): 458-474.

[4]Gilbert B, Lechowicz M J. Neutrality, niches, and dispersal in a temperate forest understory. Proceedings of the National Academy of Sciences of the United States of America, 2004, 101(20): 7651-7656.

[5]Kristiansen T, Svenning J C, Eiserhardt W L, Pedersen D, Brix H, Munch Kristiansen S, Knadel M, Grández C, Balslev H. Environment versus dispersal in the assembly of western Amazonian palm communities. Journal of Biogeography, 2012, 39(7): 1318-1332.

[6]Tuomisto H, Ruokolainen K, Yli-Halla M. Dispersal, environment, and floristic variation of western Amazonian forests. Science, 2003, 299(5604): 241-244.

[7]Hubbell S P. The unified neutral theory of biodiversity and biogeography. Princeton: Princeton University Press, 2001.

[8]Jones M M, Tuomisto H, Clark D B, Olivas P. Effects of mesoscale environmental heterogeneity and dispersal limitation on floristic variation in rain forest ferns. Journal of Ecology, 2005, 94(1): 181-195.

[9]Nekola J C, White P S. The distance decay of similarity in biogeography and ecology. Journal of Biogeography, 1999, 26(4): 867-878.

[10]Legendre P, Mi X, Ren H, Ma K, Yu M, Sun I F, He F. Partitioning beta diversity in a subtropical broad-leaved forest of China. Ecology, 2009, 90(3): 663-674.

[11]Laliberté E, Paquette A, Legendre P, Bouchard A. Assessing the scale-specific importance of niches and other spatial processes on beta diversity: a case study from a temperate forest. Oecologia, 2009, 159(2): 377-388.

[12]Harms K E, Condit R, Hubbell S P, Foster R B. Habitat associations of trees and shrubs in a 50-ha neotropical forest plot. Journal of Ecology, 2001, 89(6): 947-959.

[13]Andersen K M, Turner B L, Dalling J W. Soil-based habitat partitioning in understorey palms in lower montane tropical forests. Journal of Biogeography, 2010, 37(2): 278-292.

[14]Nakashizuka T. Species coexistence in temperate, mixed deciduous forests. Trends in Ecology & Evolution, 2001, 16(4): 205-210.

[15]Egler F E. Vegetation science concepts I. Initial floristic composition, a factor in old-field vegetation development. Vegetatio, 1954, 4(6): 412-417.

[16]Wang G H. Can the restoration of natural vegetation be accelerated on the Chinese Loess Plateau? A study of the response of the leaf carbon isotope ratio of dominant species to changing soil carbon and nitrogen levels. Ecological Research, 2006, 21(2): 188-196.

[17]Kraft N J, Valencia R, Ackerly D D. Functional traits and niche-based tree community assembly in an Amazonian forest. Science, 2008, 322(5901): 580-582.

[18]Brudvig L A, Mabry C M, Mottl L M. Dispersal, not understory light competition, limits restoration of Iowa woodland understory herbs. Restoration Ecology, 2011, 19(101): 24-31.

[19]Shurin J B, Cottenie K, Hillebrand H. Spatial autocorrelation and dispersal limitation in freshwater organisms. Oecologia, 2009, 159(1): 151-159.

[20]Freestone A L, Inouye B D. Dispersal limitation and environmental heterogeneity shape scale-dependent diversity patterns in plant communities. Ecology, 2006, 87(10): 2425-2432.

[21]刘立品. 子午岭木本植物志. 兰州:兰州大学出版社,1998.

Liu L P. Flora arborum et fruticum Ziwu Mountain. Lanzhou: Lanzhou University Press, 1998. (in Chinese)

[22]孙晓霞, 王孝安, 郭华, 田丽. 黄土高原马栏林区植物群落的多元分析与环境解释. 西北植物学报, 2006, 26(1): 150-156.

Sun X X, Wang X A, Guo H, Tian L. Multivariate analysis and environmental interpretation of the florae in Malan Forest Region of the Loess Plateau. Acta Botanica Boreali-Occidentalia Sinica, 2006, 26(1): 150-156. (in Chinese)

[23]Liang J, Wang X A, Yu Z D, Dong Z M, Wang J C. Effects of Vegetation Succession on Soil Fertility Within Farming-Plantation Ecotone in Ziwuling Mountains of the Loess Plateau in China. Agricultural Sciences in China, 2010, 9(10): 1481-1491.

[24]Legendre P, Gallagher E D. Ecologically meaningful transformations for ordination of species data. Oecologia, 2001, 129(2): 271-280.

[25]Borcard D, Legendre P. All-scale spatial analysis of ecological data by means of principal coordinates of neighbour matrices. Ecological Modelling, 2002, 153(1): 51-68.

[26]Dray S, Legendre P, Peres-Neto P R. Spatial modelling: a comprehensive framework for principal coordinate analysis of neighbour matrices (PCNM). Ecological Modelling, 2006, 196(3): 483-493.

[27]Peres-Neto P R, Legendre P, Dray S, Borcard D. Variation partitioning of species data matrices: estimation and comparison of fractions. Ecology, 2006, 87(10): 2614-2625.

[28]Chao A. Estimating the population size for capture-recapture data with unequal catchability. Biometrics, 1987, 43(4): 783-791.

[29]Dray S. Pack for: forward selection with multivariate Y by permutation under reduced model. Lyon: Laboratoire Biométrie et Biologie Évolutive, 2005.

[30]Oksanen J, Guillaume Blanchet F, Kindt R, Legendre P, O’Hara R, Simpson G, Solymos P, Stevens M, Wagner H. vegan: community ecology package v.1.17-9, 2011.

[31]Borcard D, Legendre P. SpaceMaker 2 user’s guide. Département de Sciences Biologiques, Université Montréal, Montréal, Quebec, Canada, 2004.

[32]王世雄, 王孝安, 李国庆, 郭华, 朱志红. 陕西子午岭植物群落演替过程中物种多样性变化与环境解释. 生态学报, 2010, 30(6): 1638-1647.

Wang S X, Wang X A, Li G Q, Guo H, Zhu Z H. Species diversity and environmental interpretation in the process of community succession in the Ziwu Mountain of Shaanxi Province. Acta Ecologica Sinica, 2010, 30(6): 1638-1647. (in Chinese)

[33]Fralish J S, Crooks F B, Chambers J L, Harty F M. Comparison of presettlement, second-growth and old-growth forest on six site types in the Illinois Shawnee Hills. American Midland Naturalist, 1991, 125(2): 294-309.

[34]Bruna E M. Effects of forest fragmentation on Heliconia acuminata seedling recruitment in central Amazonia. Oecologia, 2002, 132(2): 235-243.

[35]Laurance W F, Ferreira L V, Rankin-de Merona J M, Laurance S G. Rain forest fragmentation and the dynamics of Amazonian tree communities. Ecology, 1998, 79(6): 2032-2040.

[36]Jones M M, Tuomisto H, Borcard D, Legendre P, Clark D B, Olivas P C. Explaining variation in tropical plant community composition: influence of environmental and spatial data quality. Oecologia, 2008, 155(3): 593-604.

[37]Summerville K S, Conoan C J, Steichen R M. Species traits as predictors of lepidopteran composition in restored and remnant tallgrass prairies. Ecological Applications, 2006, 16(3): 891-900.

[38]Flinn K M, Gouhier T C, Lechowicz M J, Waterway M J. The role of dispersal in shaping plant community composition of wetlands within an old-growth forest. Journal of Ecology, 2010, 98(6): 1292-1299.

[39]Ricklefs R E, Latham R E. Intercontinental correlation of geographical ranges suggests stasis in ecological traits of relict genera of temperate perennial herbs. The American Naturalist, 1992, 139(6): 1305-1321.

[40]Stevens M H H, Carson W P. Resource quantity, not resource heterogeneity, maintains plant diversity. Ecology Letters, 2002, 5(3): 420-426.

[41]Grubb P J. The maintenance of species-richness in plant communities: the importance of the regeneration niche. Biological Reviews, 1977, 52(1): 107-145.

[42]Muller C H. Allelopathy as a factor in ecological process. Plant Ecology, 1969, 18(1): 348-357.

[43]Duivenvoorden J, Svenning J, Wright S. Beta diversity in tropical forests. Science, 2002, 295(5555): 636-637.

[44]Chase J M. Stochastic community assembly causes higher biodiversity in more productive environments. Science, 2010, 328(5984): 1388-1391.

[45]Chase J M. Drought mediates the importance of stochastic community assembly. Proceedings of the National Academy of Sciences, 2007, 104(44): 17430-17434.
No related articles found!
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed   
No Suggested Reading articles found!