海南尖峰岭不同热带雨林类型与物种多样性变化关联的环境因子

doi:10.3724/SP.J.1258.2013.00003

植物生态学报 ›› 2013, Vol. 37 ›› Issue (1): 26-36.DOI: 10.3724/SP.J.1258.2013.00003

海南尖峰岭不同热带雨林类型与物种多样性变化关联的环境因子

许涵¹^,², 李意德²^,^*(), 骆土寿², 陈德祥², 林明献²

¹中国林业科学研究院林木遗传育种国家重点实验室, 北京 100191
²中国林业科学研究院热带林业研究所, 广州 510520

收稿日期:2012-05-14 接受日期:2012-12-14 出版日期:2013-05-14 发布日期:2013-01-15
通讯作者: 李意德
作者简介:*(E-mail:liyide@126.com)
基金资助:
中央级公益性科研院所基本科研业务费专项“基于大样地系统的热带森林动态监测研究”(CAFYBB2011004);“尖峰岭大样地系统的数据集成与野外手册编制”(RITFYWZX201204);“海南岛热带雨林动态监测大样地建立及监测”(RITF-YWZX200902);林业公益性行业科研专项“热带雨林生物多样性维持与自然恢复策略研究”(201104057)

Environmental factors correlated with species diversity in different tropical rain forest types in Jianfengling, Hainan Island, China

XU Han¹^,², LI Yi-De²^,^*(), LUO Tu-Shou², CHEN De-Xiang², LIN Ming-Xian²

¹State Key Laboratory of Tree Genetics and Breeding, Chinese Academy of Forestry, Beijing 100191, China
²Research Institute of Tropical Forestry, Chinese Academy of Forestry, Guangzhou 510520, China

Received:2012-05-14 Accepted:2012-12-14 Online:2013-05-14 Published:2013-01-15
Contact: LI Yi-De

摘要/Abstract

摘要：

环境因子是影响物种分布并导致物种多样性形成的重要因素, 采伐后恢复的热带森林次生林和原始林的环境因子是否一致是一个很重要的问题。对于该问题的回答对长期监测热带森林次生林的变化具有重要意义。该文基于在海南尖峰岭地区设置的164个625 m²植被公里网格样地数据, 记录了每个样地的采伐历史并测定了其他的17个环境变量指标, 分析了17个环境因子之间的相关关系; 将164个样地划分成3种不同采伐历史的森林, 通过典范对应分析(CCA)探讨3种森林类型中影响物种分布的环境因子组成; 比较两种多元回归模型的优劣, 来揭示3种森林类型中影响物种丰富度形成的环境因子组成的差异。结果表明: 驱动海南尖峰岭地区物种分布并导致物种多样性差异的环境因子在森林采伐前后并不是一成不变的, 而是与森林采伐历史有关联的。除了人为森林采伐干扰外, 海拔梯度是形成海南尖峰岭热带天然林物种多样性的最重要因素。CCA分析显示: 原始林中, 物种分布与海拔、土壤交换性钙和交换性镁含量3个环境因子有较密切的关系, 也与4个土壤物理性质环境因子(土壤密度、土壤最大持水能力、毛细管持水量和毛管孔隙度)关系密切; 森林采伐后的恢复森林中, 土壤全磷和速效磷含量对物种分布的影响增强, 但皆伐后土壤交换性钙和交换性镁含量对物种分布的影响减弱。多元回归分析显示: 原始林的物种丰富度与海拔和土壤交换性钙含量显著相关, 径级择伐后恢复热带天然林的物种丰富度和海拔、土壤全磷含量和速效钾含量显著相关, 皆伐后恢复热带天然林的物种丰富度仅和海拔显著相关。研究结果还显示, 如果数据中存在空间自相关, 建立多元回归模型时应该考虑数据中的空间自相关属性, 虽然它并不总是存在的。

关键词: 环境因子, 森林采伐, 尖峰岭, 空间自相关, 物种分布, 物种多样性

Abstract:

Aims Environmental factors are key factors impacting species distribution and determining species richness. An important question is whether the major environmental factor are the same in old-growth forests and secondary forests produced by logging. This question is very important for monitoring long-term changes in secondary tropical rain forests.
Methods A unique, robust data set consisting of 164 625 m² quadrats in a 160 km² tropical rainforest was set up from August 2007 to June 2009 in the middle of the Jianfengling Natural Reserve, Hainan Island, China. Forest logging history was determined and 17 environmental factors were measured for each quadrat. First, we analyzed the relationship among these 17 factors. Then, these quadrats were classified into three forest types with different logging history: old-growth forests, diameter-limit logged forests and clear-cut forests. Canonical correspondence analysis (CCA) was used to analyze the environmental factors impacting species distributions. Step-forward multiple regression was used with and without considering spatial autocorrelation in the data set to disclose which environmental factors determined species richness.
Important findings The environmental factors impacting species distribution and determining species richness changed because of differences of forests logging history. Elevation is the second most important factor influencing patterns of species diversity. CCA showed that species distribution in old-growth forests is closely related to elevation, soil exchangeable calcium content, soil exchangeable magnesium content and four soil physical factors (soil density, maximum water holding content, capillary water-holding content and capillary porosity). Importance of soil total phosphorous content and available phosphorous content was greater in logged forests, but the importance of soil exchangeable calcium content and exchangeable magnesium content was lower in clear-cut forests. Multiple regression analysis also showed that species richness was significantly correlated with elevation and soil exchangeable calcium in the old-growth forests. While species richness was correlated with elevation, soil total phosphorous content and soil available potassium content in the diameter-limit logged forests and was only correlated with elevation in the clear-cut forests. Furthermore, it is suggested it is better to compare the spatial autocorrelation models with other models to describe the relationship between environmental factors and species richness, even it does not always exist in the ecological data set with spatial characteristics.

Key words: environmental factor, forest logging, Jianfengling, spatial autocorrelation, species distribution, species diversity

许涵, 李意德, 骆土寿, 陈德祥, 林明献. 海南尖峰岭不同热带雨林类型与物种多样性变化关联的环境因子. 植物生态学报, 2013, 37(1): 26-36. DOI: 10.3724/SP.J.1258.2013.00003

XU Han, LI Yi-De, LUO Tu-Shou, CHEN De-Xiang, LIN Ming-Xian. Environmental factors correlated with species diversity in different tropical rain forest types in Jianfengling, Hainan Island, China. Chinese Journal of Plant Ecology, 2013, 37(1): 26-36. DOI: 10.3724/SP.J.1258.2013.00003

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图/表 8

参考文献 35

[1]	Badgley C, Fox DL (2000). Ecological biogeography of North American mammals: species density and ecological structure in relation to environmental gradients. Journal of Biogeography, 27, 1437-1467.
[2]	Beck J, Chey VK (2008). Explaining the elevational diversity pattern of geometrid moths from Borneo: a test of five hypotheses. Journal of Biogeography, 35, 1452-1464.
[3]	Berry NJ, Phillips OL, Ong RC, Hamer KC (2008). Impacts of selective logging on tree diversity across a rainforest landscape: the importance of spatial scale. Landscape Ecology, 23, 915-929.
[4]	Brown KA, Gurevitch J (2004). Long-term impacts of logging on forest diversity in Madagascar. Proceedings of the National Academy of Sciences of the United States of America, 101, 6045-6049. DOI URL PMID
[5]	Cannon CH, Peart DR, Leighton M (1998). Tree species diversity in commercially logged Bornean rainforest. Science, 281, 1366-1368. URL PMID
[6]	Cramer MJ, Willig MR (2002). Habitat heterogeneity, habitat associations, and rodent species diversity in a sand- shinnery-oak landscape. Journal of Mammalogy, 83, 743-753.
[7]	de Deyn GB, Raaijmakers CE, van der Putten WH (2004). Plant community development is affected by nutrients and soil biota. Journal of Ecology, 92, 824-834.
[8]	Diniz-Filho JAF, Bini LM, Hawkins BA (2003). Spatial autocorrelation and red herrings in geographical ecology. Global Ecology and Biogeography, 12, 53-64.
[9]	Diniz-Filho JAF, de Campos Telles MP (2002). Spatial autocorrelation analysis and the identification of operational units for conservation in continuous populations. Conservation Biology, 16, 924-935.
[10]	Diniz-Filho JAF, Rangel TFLVB, Hawkins BA (2004). A test of multiple hypotheses for the species richness gradient of South American owls. Oecologia, 140, 633-638. DOI URL PMID
[11]	Dormann CF (2007). Effects of incorporating spatial autocorrelation into the analysis of species distribution data. Global Ecology and Biogeography, 16, 129-138.
[12]	Dumbrell AJ, Clark EJ, Frost GA, Randell TE, Pitchford JW, Hill JK (2008). Changes in species diversity following habitat disturbance are dependent on spatial scale: theoretical and empirical evidence. Journal of Applied Ecology, 45, 1531-1539.
[13]	Firn J, Erskine PD, Lamb D (2007). Woody species diversity influences productivity and soil nutrient availability in tropical plantations. Oecologia, 154, 521-533. DOI URL PMID
[14]	Foody GM (2004). Spatial nonstationarity and scale- dependency in the relationship between species richness and environmental determinants for the sub-Saharan endemic avifauna. Global Ecology and Biogeography, 13, 315-320.
[15]	Hawkins BA, Field R, Cornell HV, Currie DJ, Guégan JF, Kaufman DM, Kerr JT, Mittelbach GG, Oberdorff T, O’Brien EM, Porter EE, Turner JRG (2003). Energy, water, and broad-scale geographic patterns of species richness. Ecology, 84, 3105-3117.
[16]	He JS, Chen WL (1997). A review of gradient changes in species diversity of land plant communities. Acta Ecologica Sinica, 17, 91-99. (in Chinses with English abstract)
	[ 贺金生, 陈伟烈 (1997). 陆地植物群落物种多样性的梯度变化特征. 生态学报, 17, 91-99.]
[17]	Hurlbert AH, White EP (2005). Disparity between range map- and survey-based analyses of species richness: patterns, processes and implications. Ecology Letters, 8, 319-327.
[18]	Jiang YX, Lu JP (1991). Tropical Forest Ecosystems of Jianfengling, Hainan Island, China. Science Press, Beijing. 29-42. (in Chinese)
	[ 蒋有绪, 卢俊培 (1991). 中国海南岛尖峰岭热带林生态系统. 科学出版社, 北京. 29-42.]
[19]	Kaboli M, Guillaumet A, Prodon R (2006). Avifaunal gradients in two arid zones of central Iran in relation to vegetation, climate, and topography. Journal of Biogeography, 33, 133-144.
[20]	Kühn I (2007). Incorporating spatial autocorrelation may invert observed patterns. Diversity and Distributions, 13, 66-69.
[21]	Legendre P, Legendre L (1998). Numerical Ecology 2nd edn. Elsevier Science, Amsterdam.
[22]	Li YD, Chen BF, Zhou GY, Wu ZM, Zeng QB, Luo TS, Huang SN, Xie MD, Huang Q (2002). Research on Tropical Forest and Biodiversity Conservation in Hainan Island, China. Chinese Forest Publishing House, Beijing. 47-51. (in Chinese)
	[ 李意德, 陈步峰, 周光益, 吴仲民, 曾庆波, 骆土寿, 黄世能, 谢明东, 黄全 (2002). 中国海南岛热带森林及其生物多样性保护研究. 中国林业出版社, 北京. 47-51.]
[23]	Lomolino MV (2001). Elevation gradients of species-density: historical and prospective views. Global Ecology and Biogeography Letters, 10, 3-13.
[24]	Paoli GD, Currant LM, Zak DR (2006). Soil nutrients and beta diversity in the Bornean Dipterocarpaceae: evidence for niche partitioning by tropical rain forest trees. Journal of Ecology, 94, 157-170.
[25]	Pimm SL, Brown JH (2004). Domains of diversity. Science, 304, 831-833. URL PMID
[26]	Qian H, Wang S, Li Y, Wang X (2009). Breeding bird diversity in relation to environmental gradients in China. Acta Oecologica, 35, 819-823.
[27]	Rahbek C, Graves GR (2000). Detection of macro-ecological patterns in South American humming birds is affected by spatial scale. Proceedings of the Royal Society of London Series B, 267, 2259-2265. DOI URL PMID
[28]	Rossi JP, Queneherve P (1998). Relating species density to environmental variables in presence of spatial autocorrela- tion: a study case on soil nematodes distribution. Ecography, 21, 117-123.
[29]	Rowe RJ, Lidgard S (2009). Elevational gradients and species richness: do methods change pattern perception? Global Ecology and Biogeography, 18, 163-177.
[30]	Tognelli MF, Kelt DA (2004). Analysis of determinants of mammalian species richness in South America using spatial autoregressive models. Ecography, 27, 427-436.
[31]	van Rensburg BJ, Chown SL, Gaston KJ (2002). Species richness, environmental correlates, and spatial scale: a test using South African birds. The American Naturalist, 159, 566-577. URL PMID
[32]	Vetaas OR, Grytnes JA (2002). Distribution of vascular plant species richness and endemic richness along the Himalayan elevation gradient in Nepal. Global Ecology and Biogeography, 11, 291-301.
[33]	Wang SX, Wang XA, Li GQ, Guo H, Zhu ZH (2010). Species diversity and environmental interpretation in the process of community succession in the Ziwu Mountain of Shaanxi Province. Acta Ecologica Sinica, 30, 1638-1647. (in Chinses with English abstract)
	[ 王世雄, 王孝安, 李国庆, 郭华, 朱志红 (2010). 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, 30, 1638-1647.]
[34]	Xu H, Li YD, Luo TS, Chen DX, Lin MX, Yang H (2012). Impacts of forest logging on the species diversity of endemic seed plants from Hainan Island. Biodiversity Science, 20, 168-176. (in Chinses with English abstract)
	[ 许涵, 李意德, 骆土寿, 陈德祥, 林明献, 杨怀 (2012). 森林采伐对尖峰岭海南特有种子植物多样性的影响. 生物多样性, 20, 168-176.]
[35]	Xu YJ, Chen YN, Li WH, Fu AH, Ma XD, Gui DW, Chen YP (2010). Distribution pattern and environmental interpretation of plant species diversity in the mountainous region of Ili River Valley, Xinjiang, China. Chinese Journal of Plant Ecology, 34, 1142-1154. (in Chinses with English abstract)
	[ 徐远杰, 陈亚宁, 李卫红, 付爱红, 马晓东, 桂东伟, 陈亚鹏 (2010). 伊黎河谷山地植物群落物种多样性分布格局及环境解释. 植物生态学报, 34, 1142-1154.]

环境因子 Environmental factor	海拔 Elevation	坡度 Slope degree	坡向 Slope aspect	坡位 Slope position	土壤有机碳含量 Soil organic carbon content	土壤全氮含量 Soil total nitrogen content	土壤全磷含量 Soil total phosphorus content	土壤全钾含量 Soil total potassium content	土壤交换性钙含量 Soil exchangeable calcium content	土壤交换性镁含量 Soil exchangeable magnesium content	土壤速效钾含量 Soil available potassium content	土壤碱解氮含量 Soil alkali dispelled nitrogen content	土壤速效磷含量 Soil available phosphorus content	土壤密度 Soil density	土壤最大持水量 Soil maximum water holding content	土壤毛细管持水量 Soil capillary water holding content	土壤毛管孔隙度 Soil capillary porosity
海拔 Elevation	-
坡度 Slope degree	0.006
坡向 Slope aspect	-0.002	-0.298^**
坡位 Slope position	0.009	-0.190^*	0.146
土壤有机碳含量 Soil organic carbon content	0.352^**	-0.011	0.019	-0.109
土壤全氮含量 Soil total nitrogen content	0.366^**	0.070	0.079	-0.013	0.775^**
土壤全磷含量 Soil total phosphorus content	0.079	0.029	0.123	0.138	0.276^**	0.452^**
土壤全钾含量 Soil total potassium content	-0.230^**	0.309^**	-0.098	-0.029	-0.144	-0.031	0.104
土壤交换性钙含量 Soil exchangeable calcium content	-0.126	0.037	0.017	0.097	0.069	0.157*	0.718^**	0.130
土壤交换性镁含量 Soil exchangeable magnesium content	-0.238^**	0.072	-0.010	0.055	0.037	0.130	0.691^**	0.242^**	0.932^**
土壤速效钾含量 Soil available potassium content	-0.409^**	0.216^**	-0.171^*	-0.070	-0.155^*	-0.127	-0.041	0.620^**	0.131	0.307^**
土壤碱解氮含量 Soil alkali dispelled nitrogen content	0.471^**	-0.034	0.131	-0.018	0.521^**	0.667^**	0.444^**	-0.109	0.074	0.017	-0.180^*
土壤速效磷含量 Soil available phosphorus content	-0.204^**	0.083	0.032	0.098	0.134	0.247^**	0.587^**	0.306^**	0.480^**	0.498^**	0.136	0.172^*
土壤密度 Soil density	-0.759^**	0.071	-0.033	0.062	-0.345^**	-0.371^**	-0.186^*	0.327^**	0.045	0.168^*	0.403^**	-0.597^**	0.171^*
土壤最大持水量 Soil maximum water holding content	0.570^**	-0.109	0.138	-0.019	0.142	0.261^**	0.202^**	-0.239^**	0.065	-0.032	-0.280^**	0.431^**	-0.175^*	-0.691^**
土壤毛细管持水量 Soil capillary water holding content	0.497^**	-0.169^*	0.173^*	0.029	0.107	0.161^*	0.098	-0.304^**	0.064	-0.058	-0.396^**	0.198^*	-0.304^**	-0.403^**	0.743^**
土壤毛管孔隙度 Soil capillary porosity	0.499^**	-0.167^*	0.173^*	0.026	0.109	0.161^*	0.097	-0.304^**	0.062	-0.060	-0.395^**	0.200^*	-0.306^**	-0.405^**	0.743^**	1.000^**	-

环境因子 Environmental factor	海拔 Elevation	坡度 Slope degree	坡向 Slope aspect	坡位 Slope position	土壤有机碳含量 Soil organic carbon content	土壤全氮含量 Soil total nitrogen content	土壤全磷含量 Soil total phosphorus content	土壤全钾含量 Soil total potassium content	土壤交换性钙含量 Soil exchangeable calcium content	土壤交换性镁含量 Soil exchangeable magnesium content	土壤速效钾含量 Soil available potassium content	土壤碱解氮含量 Soil alkali dispelled nitrogen content	土壤速效磷含量 Soil available phosphorus content	土壤密度 Soil density	土壤最大持水量 Soil maximum water holding content	土壤毛细管持水量 Soil capillary water holding content	土壤毛管孔隙度 Soil capillary porosity
海拔 Elevation	-
坡度 Slope degree	0.006
坡向 Slope aspect	-0.002	-0.298^**
坡位 Slope position	0.009	-0.190^*	0.146
土壤有机碳含量 Soil organic carbon content	0.352^**	-0.011	0.019	-0.109
土壤全氮含量 Soil total nitrogen content	0.366^**	0.070	0.079	-0.013	0.775^**
土壤全磷含量 Soil total phosphorus content	0.079	0.029	0.123	0.138	0.276^**	0.452^**
土壤全钾含量 Soil total potassium content	-0.230^**	0.309^**	-0.098	-0.029	-0.144	-0.031	0.104
土壤交换性钙含量 Soil exchangeable calcium content	-0.126	0.037	0.017	0.097	0.069	0.157*	0.718^**	0.130
土壤交换性镁含量 Soil exchangeable magnesium content	-0.238^**	0.072	-0.010	0.055	0.037	0.130	0.691^**	0.242^**	0.932^**
土壤速效钾含量 Soil available potassium content	-0.409^**	0.216^**	-0.171^*	-0.070	-0.155^*	-0.127	-0.041	0.620^**	0.131	0.307^**
土壤碱解氮含量 Soil alkali dispelled nitrogen content	0.471^**	-0.034	0.131	-0.018	0.521^**	0.667^**	0.444^**	-0.109	0.074	0.017	-0.180^*
土壤速效磷含量 Soil available phosphorus content	-0.204^**	0.083	0.032	0.098	0.134	0.247^**	0.587^**	0.306^**	0.480^**	0.498^**	0.136	0.172^*
土壤密度 Soil density	-0.759^**	0.071	-0.033	0.062	-0.345^**	-0.371^**	-0.186^*	0.327^**	0.045	0.168^*	0.403^**	-0.597^**	0.171^*
土壤最大持水量 Soil maximum water holding content	0.570^**	-0.109	0.138	-0.019	0.142	0.261^**	0.202^**	-0.239^**	0.065	-0.032	-0.280^**	0.431^**	-0.175^*	-0.691^**
土壤毛细管持水量 Soil capillary water holding content	0.497^**	-0.169^*	0.173^*	0.029	0.107	0.161^*	0.098	-0.304^**	0.064	-0.058	-0.396^**	0.198^*	-0.304^**	-0.403^**	0.743^**
土壤毛管孔隙度 Soil capillary porosity	0.499^**	-0.167^*	0.173^*	0.026	0.109	0.161^*	0.097	-0.304^**	0.062	-0.060	-0.395^**	0.200^*	-0.306^**	-0.405^**	0.743^**	1.000^**	-

环境因子 Environmental factor	原始林 Old-growth forest			径级择伐后恢复森林 Recovered forest after diameter-limit logging			皆伐后恢复森林 Recovered forest after clear-cutting
环境因子 Environmental factor	第1轴 Axis 1	第2轴 Axis 2	第3轴Axis 3	第1轴 Axis 1	第2轴 Axis 2	第3轴Axis 3	第1轴 Axis 1	第2轴 Axis 2	第3轴 Axis 3
海拔 Elevation	0.01	-0.18	0.31	-0.03	0.36	0.15	0.11	-0.32	-0.07
坡度 Slope degree	-0.14	0.12	-0.39	0.03	-0.03	0.04	-0.04	-0.02	0.42
坡向 Slope aspect	-0.01	-0.09	-0.53	0.10	-0.21	-0.63	-0.09	-0.12	0.38
坡位 Slope position	0.34	-0.83	-0.11	-0.09	0.87	0.08	-0.60	-0.51	0.24
土壤有机碳含量 Soil organic carbon content	0.11	-0.54	0.11	0.07	0.14	0.26	-0.05	0.54	-0.18
土壤全氮含量 Soil total nitrogen content	-0.07	-0.57	-0.11	0.10	0.31	0.07	-0.21	-0.02	0.28
土壤全磷含量 Soil total phosphorus content	-0.26	-0.10	-0.54	0.79	0.12	-0.33	0.08	0.09	0.76
土壤全钾含量 Soil total potassium content	-0.27	0.11	-0.25	0.01	-0.23	-0.50	0.10	-0.33	0.14
土壤交换性钙含量 Soil exchangeable calcium content	-0.91	-0.13	-0.08	0.97	0.04	-0.11	0.13	0.14	-0.42
土壤交换性镁含量 Soil exchangeable magnesium content	-0.51	0.23	-0.24	0.92	-0.04	-0.17	0.32	0.37	-0.33
土壤速效钾含量 Soil available potassium content	-0.15	0.26	-0.23	-0.04	-0.14	-0.43	0.20	0.23	-0.45
土壤碱解氮含量 Soil alkali dispelled nitrogen content	0.04	-0.61	-0.21	0.09	0.53	0.05	-0.46	-0.19	0.55
土壤速效磷含量 Soil available phosphorus content	-0.34	0.29	-0.31	0.60	-0.27	-0.14	0.81	-0.13	0.47
土壤密度 Soil density	-0.29	0.65	0.23	-0.04	-0.63	-0.18	0.59	0.26	-0.49
土壤最大持水量 Soil maximum water holding content	0.17	-0.56	-0.38	0.11	0.68	0.05	-0.35	-0.52	0.37
土壤毛细管持水量 Soil capillary water holding content	0.15	-0.65	-0.03	0.14	0.51	0.15	-0.25	-0.60	0.20
土壤毛管孔隙度 Soil capillary porosity	0.15	-0.65	-0.03	0.13	0.51	0.15	-0.26	-0.60	0.20

环境因子 Environmental factor	原始林 Old-growth forest			径级择伐后恢复森林 Recovered forest after diameter-limit logging			皆伐后恢复森林 Recovered forest after clear-cutting
环境因子 Environmental factor	第1轴 Axis 1	第2轴 Axis 2	第3轴Axis 3	第1轴 Axis 1	第2轴 Axis 2	第3轴Axis 3	第1轴 Axis 1	第2轴 Axis 2	第3轴 Axis 3
海拔 Elevation	0.01	-0.18	0.31	-0.03	0.36	0.15	0.11	-0.32	-0.07
坡度 Slope degree	-0.14	0.12	-0.39	0.03	-0.03	0.04	-0.04	-0.02	0.42
坡向 Slope aspect	-0.01	-0.09	-0.53	0.10	-0.21	-0.63	-0.09	-0.12	0.38
坡位 Slope position	0.34	-0.83	-0.11	-0.09	0.87	0.08	-0.60	-0.51	0.24
土壤有机碳含量 Soil organic carbon content	0.11	-0.54	0.11	0.07	0.14	0.26	-0.05	0.54	-0.18
土壤全氮含量 Soil total nitrogen content	-0.07	-0.57	-0.11	0.10	0.31	0.07	-0.21	-0.02	0.28
土壤全磷含量 Soil total phosphorus content	-0.26	-0.10	-0.54	0.79	0.12	-0.33	0.08	0.09	0.76
土壤全钾含量 Soil total potassium content	-0.27	0.11	-0.25	0.01	-0.23	-0.50	0.10	-0.33	0.14
土壤交换性钙含量 Soil exchangeable calcium content	-0.91	-0.13	-0.08	0.97	0.04	-0.11	0.13	0.14	-0.42
土壤交换性镁含量 Soil exchangeable magnesium content	-0.51	0.23	-0.24	0.92	-0.04	-0.17	0.32	0.37	-0.33
土壤速效钾含量 Soil available potassium content	-0.15	0.26	-0.23	-0.04	-0.14	-0.43	0.20	0.23	-0.45
土壤碱解氮含量 Soil alkali dispelled nitrogen content	0.04	-0.61	-0.21	0.09	0.53	0.05	-0.46	-0.19	0.55
土壤速效磷含量 Soil available phosphorus content	-0.34	0.29	-0.31	0.60	-0.27	-0.14	0.81	-0.13	0.47
土壤密度 Soil density	-0.29	0.65	0.23	-0.04	-0.63	-0.18	0.59	0.26	-0.49
土壤最大持水量 Soil maximum water holding content	0.17	-0.56	-0.38	0.11	0.68	0.05	-0.35	-0.52	0.37
土壤毛细管持水量 Soil capillary water holding content	0.15	-0.65	-0.03	0.14	0.51	0.15	-0.25	-0.60	0.20
土壤毛管孔隙度 Soil capillary porosity	0.15	-0.65	-0.03	0.13	0.51	0.15	-0.26	-0.60	0.20

环境因子 Environmental factor	普通最小二乘法模型 Ordinary least-squares model			联立空间自相关模型 Spatial simultaneous autoregressive error model
环境因子 Environmental factor	估计值±标准误差 Estimated value ± SE	t值 t-value	显著性检验P_r(>\|t\|)	估计值±标准误差 Estimated value ± SE	t值 t-value	显著性检验 P_r(>\|t\|)
截距 Intercept	50.838 ± 6.561	7.749	<0.001	51.120 ± 6.277	8.144	<0.001
海拔 Elevation	0.037 ± 0.007	5.021	<0.001	0.037 ± 0.007	5.206	<0.001
土壤交换性钙 Soil exchangeable calcium content	-12.629 ± 3.537	-3.570	<0.001	-12.779 ± 3.414	-3.743	<0.001

海南尖峰岭不同热带雨林类型与物种多样性变化关联的环境因子

Environmental factors correlated with species diversity in different tropical rain forest types in Jianfengling, Hainan Island, China

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