植物生态学报 ›› 2006, Vol. 30 ›› Issue (4): 576-584.DOI: 10.17521/cjpe.2006.0076
收稿日期:
2005-02-25
接受日期:
2005-10-11
出版日期:
2006-02-25
发布日期:
2006-07-30
通讯作者:
李博
作者简介:
*E-mail:bool @fudan.edu.cn基金资助:
WU Xiao-Wen, LUO Jing, CHEN Jia-Kuan, LI Bo*()
Received:
2005-02-25
Accepted:
2005-10-11
Online:
2006-02-25
Published:
2006-07-30
Contact:
LI Bo
摘要:
认识区域尺度上外来入侵植物的分布格局及其成因对预测入侵的影响和入侵种的管理具有重要意义。该文采用聚类分析和排序的方法分析了我国外来入侵植物的空间格局,并利用多元线性逐步回归和典范对应分析探讨了自然环境因子和人类活动强度对中国32个省级空间单位(省市自治区,不包括香港和澳门)中外来入侵植物分布的影响。结果表明,中国各省外来入侵植物物种数从南到北逐渐减少,导致这一格局的主要因子为无霜期;各省外来入侵植物物种密度由东南海岸向内陆递减,造成这一趋势的主要影响因素为交通密度;纬度是解释中国各省外来入侵植物物种组成变异的主要因子,因此中国32个省区可归为低、中、高纬度区3大类型。在此基础上预测中国东南部地区有遭受更多外来植物入侵的可能;此外,交通发达的区域也将成为外来植物入侵的热点区,应该引起有关部门的重视。
吴晓雯, 罗晶, 陈家宽, 李博. 中国外来入侵植物的分布格局及其与环境因子和人类活动的关系. 植物生态学报, 2006, 30(4): 576-584. DOI: 10.17521/cjpe.2006.0076
WU Xiao-Wen, LUO Jing, CHEN Jia-Kuan, LI Bo. SPATIAL PATTERNS OF INVASIVE ALIEN PLANTS IN CHINA AND ITS RELATIONSHIP WITH ENVIRONMENTAL AND ANTHROPOLOGICAL FACTORS. Chinese Journal of Plant Ecology, 2006, 30(4): 576-584. DOI: 10.17521/cjpe.2006.0076
变量 Variables | 单位 Units | 数据转换 Data transformation |
---|---|---|
环境变量 Environmental factors | ||
纬度 Latitude (LTD) | 度 (°) | — |
经度 Longitude (LGD) | 度 (°) | — |
省面积 Area of province (PAR) | 万平方公里 (104 km2) | 对数转换ln |
1月平均气温 Mean temperature in January (MT1) | 摄氏度 (℃) | — |
7月平均气温 Mean temperature in July (MT7) | 摄氏度 (℃) | — |
年降雨量 Annual precipitation (APP) | 毫米 (mm) | — |
无霜期 Frost-free days (FFD) | 天 Days | — |
人类影响 Anthropological factors | ||
人口密度 Population density (PLD) | 个数/平方公里 Persons·km-2 | 平方根转换 Square root |
交通密度 Transport density (TPD) | 线路长/万平方公里 km·104 km-2 | — |
省内年度生产总值 Values of annual gross production (GDP) | 亿元 (108 RMB) | 对数转换 ln |
进口货物总额 Values of imported goods (VIC) | 万美元 (104 US dollars) | 对数(平方根转换) ln (Square root) |
外来游客人数 Number of foreign tourists (NFT) | 万人 (104 persons) | 对数转换 ln |
省内自然保护区面积 Area of nature reserves (ANR) | 平方公里 (km2) | 对数转换 ln |
省内保护区的面积比例 Percentage of areas protected (PAP) | 百分比 (%) | 对数转换 ln |
表1 反映中国各省环境因子和人类活动的变量
Table 1 Variables reflecting environmental features and the intensity of human activities in province, China
变量 Variables | 单位 Units | 数据转换 Data transformation |
---|---|---|
环境变量 Environmental factors | ||
纬度 Latitude (LTD) | 度 (°) | — |
经度 Longitude (LGD) | 度 (°) | — |
省面积 Area of province (PAR) | 万平方公里 (104 km2) | 对数转换ln |
1月平均气温 Mean temperature in January (MT1) | 摄氏度 (℃) | — |
7月平均气温 Mean temperature in July (MT7) | 摄氏度 (℃) | — |
年降雨量 Annual precipitation (APP) | 毫米 (mm) | — |
无霜期 Frost-free days (FFD) | 天 Days | — |
人类影响 Anthropological factors | ||
人口密度 Population density (PLD) | 个数/平方公里 Persons·km-2 | 平方根转换 Square root |
交通密度 Transport density (TPD) | 线路长/万平方公里 km·104 km-2 | — |
省内年度生产总值 Values of annual gross production (GDP) | 亿元 (108 RMB) | 对数转换 ln |
进口货物总额 Values of imported goods (VIC) | 万美元 (104 US dollars) | 对数(平方根转换) ln (Square root) |
外来游客人数 Number of foreign tourists (NFT) | 万人 (104 persons) | 对数转换 ln |
省内自然保护区面积 Area of nature reserves (ANR) | 平方公里 (km2) | 对数转换 ln |
省内保护区的面积比例 Percentage of areas protected (PAP) | 百分比 (%) | 对数转换 ln |
图1 中国外来入侵植物的分布格局 a: 外来入侵植物物种数的空间变异 Number of invasive alien plant species in each province b: 外来入侵植物物种密度的空间变异 Density of invasive alien plants in each province
Fig.1 Distribution of invasive alien plants in China
图2 32个省市的聚类分析图(虚线将32个省市划分为3组) 1. 安徽 Anhui 2. 北京 Beijing 3. 重庆 Chongqing 4. 福建 Fujian 5. 甘肃 Gansu 6. 广东 Guangdong 7. 广西 Guangxi 8. 贵州 Guizhou 9. 海南 Hainan 10. 河北 Hebei 11. 河南 Henan 12. 黑龙江 Heilongjiang 13. 湖北 Hubei 14. 湖南 Hunan 15. 吉林 Jilin 16. 江苏 Jiangsu 17. 江西 Jiangxi 18. 辽宁 Liaoning 19. 内蒙古 Neimenggu 20. 宁夏 Ningxia 21. 青海 Qinghai 22. 山东 Shandong 23. 山西 Shanxi 24. 陕西 Shaanxi 25. 上海 Shanghai 26. 四川 Sichuan 27. 天津 Tianjin 28. 西藏 Xizang 29. 新疆 Xinjiang 30. 云南 Yunnan 31. 浙江 Zhejiang 32. 台湾 Taiwan
Fig.2 Dendrogram of the 32 provinces based on the distribution patterns of invasive alien plants (Dashed line divides 32 provinces into 3 types)
NIS | ID | PAR | LTD | LGD | MT1 | MT7 | APP | FFD | PLD | TPD | GDP | VIC | NFT | ANR | PAP | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
NIS | 1.00 | |||||||||||||||
ID | - | 1.00 | ||||||||||||||
PAR | -0.34ns | - | 1.00 | |||||||||||||
LTD | -0.86*** | -0.19ns | - | 1.00 | ||||||||||||
LGD | 0.13ns | 0.30ns | - | 0.14ns | 1.00 | |||||||||||
MT1 | 0.82*** | 0.32ns | - | -0.87*** | 0.17ns | 1.00 | ||||||||||
MT7 | 0.45* | 0.30ns | - | -0.34ns | -0.49** | 0.55** | 1.00 | |||||||||
APP | 0.85*** | 0.22ns | - | -0.87*** | 0.14ns | 0.81*** | 0.37* | 1.00 | ||||||||
FFD | 0.87*** | 0.63*** | - | -0.83*** | 0.12 | 0.86*** | 0.64*** | 0.74*** | 1.00 | |||||||
PLD | 0.10ns | 0.91*** | - | -0.09ns | 0.40* | 0.25ns | 0.41* | 0.14ns | 0.34 | 1.00 | ||||||
TPD | 0.39* | 0.82*** | - | -0.29ns | 0.54** | 0.53** | 0.60*** | 0.37* | 0.44* | 0.85*** | 1.00 | |||||
GDP | 0.41* | 0.22ns | -0.28ns | -0.28ns | 0.37* | 0.37* | 0.32ns | 0.41* | 0.42* | 0.26ns | 0.46** | 1.00 | ||||
VIC | 0.42* | 0.37* | -0.30ns | -0.29ns | 0.28ns | 0.40* | 0.23ns | 0.38* | 0.36* | 0.32ns | 0.53** | 0.88*** | 1.00 | |||
NFT | 0.50** | 0.16ns | -0.16ns | -0.32ns | 0.18ns | 0.36* | 0.25ns | 0.30ns | 0.50** | 0.20ns | 0.38* | 0.41* | 0.62*** | 1.00 | ||
ANR | -0.28ns | -0.21ns | 0.83*** | 0.13ns | -0.70*** | -0.43* | -0.76*** | -0.15ns | -0.27 | -0.32ns | -0.51** | -0.26ns | -0.15ns | -0.12ns | 1.00 | |
PAP | -0.29ns | -0.03ns | - | 0.14ns | -0.52** | -0.31ns | -0.78*** | -0.15ns | -0.23 | -0.15ns | -0.35ns | -0.12ns | 0.00ns | -0.15ns | - | 1.00 |
表2 中国各省外来入侵植物物种数和密度与环境因子及人类活动因子的关系
Table 2 Half-matrix of Pearson correlation coefficient of NIS and ID and environmental and anthropological variables
NIS | ID | PAR | LTD | LGD | MT1 | MT7 | APP | FFD | PLD | TPD | GDP | VIC | NFT | ANR | PAP | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
NIS | 1.00 | |||||||||||||||
ID | - | 1.00 | ||||||||||||||
PAR | -0.34ns | - | 1.00 | |||||||||||||
LTD | -0.86*** | -0.19ns | - | 1.00 | ||||||||||||
LGD | 0.13ns | 0.30ns | - | 0.14ns | 1.00 | |||||||||||
MT1 | 0.82*** | 0.32ns | - | -0.87*** | 0.17ns | 1.00 | ||||||||||
MT7 | 0.45* | 0.30ns | - | -0.34ns | -0.49** | 0.55** | 1.00 | |||||||||
APP | 0.85*** | 0.22ns | - | -0.87*** | 0.14ns | 0.81*** | 0.37* | 1.00 | ||||||||
FFD | 0.87*** | 0.63*** | - | -0.83*** | 0.12 | 0.86*** | 0.64*** | 0.74*** | 1.00 | |||||||
PLD | 0.10ns | 0.91*** | - | -0.09ns | 0.40* | 0.25ns | 0.41* | 0.14ns | 0.34 | 1.00 | ||||||
TPD | 0.39* | 0.82*** | - | -0.29ns | 0.54** | 0.53** | 0.60*** | 0.37* | 0.44* | 0.85*** | 1.00 | |||||
GDP | 0.41* | 0.22ns | -0.28ns | -0.28ns | 0.37* | 0.37* | 0.32ns | 0.41* | 0.42* | 0.26ns | 0.46** | 1.00 | ||||
VIC | 0.42* | 0.37* | -0.30ns | -0.29ns | 0.28ns | 0.40* | 0.23ns | 0.38* | 0.36* | 0.32ns | 0.53** | 0.88*** | 1.00 | |||
NFT | 0.50** | 0.16ns | -0.16ns | -0.32ns | 0.18ns | 0.36* | 0.25ns | 0.30ns | 0.50** | 0.20ns | 0.38* | 0.41* | 0.62*** | 1.00 | ||
ANR | -0.28ns | -0.21ns | 0.83*** | 0.13ns | -0.70*** | -0.43* | -0.76*** | -0.15ns | -0.27 | -0.32ns | -0.51** | -0.26ns | -0.15ns | -0.12ns | 1.00 | |
PAP | -0.29ns | -0.03ns | - | 0.14ns | -0.52** | -0.31ns | -0.78*** | -0.15ns | -0.23 | -0.15ns | -0.35ns | -0.12ns | 0.00ns | -0.15ns | - | 1.00 |
回归系数 Regression coefficient | 标准化系数 Standardized coefficient | F值 F-value | 显著性水平 Significance | 累积解释方差 Accumulative variance explained (%) | |
---|---|---|---|---|---|
所有的变量All variables,r=0.96,p<0.001 | |||||
截距 Intercept | 18.53 | p<0.01 | |||
无霜期FFD | 0.064 | 0.28 | 95.37 | p<0.001 | 91.1 |
年降雨量APP | 0.002 | 0.06 | 18.02 | p<0.001 | 85.2 |
外来游客人数NFT | 3.590 | 0.27 | 6.79 | p<0.05 | 88.1 |
人口密度PLD | -0.479 | -0.26 | 7.12 | p<0.05 | 90.6 |
纬度LTD | -1.440 | -0.58 | 4.44 | p<0.05 | 91.2 |
表3 外来入侵植物物种数和环境因子及人类活动因子的逐步回归分析结果
Table 3 Results of multiple stepwise regression between NIS and environmental and anthropological factors
回归系数 Regression coefficient | 标准化系数 Standardized coefficient | F值 F-value | 显著性水平 Significance | 累积解释方差 Accumulative variance explained (%) | |
---|---|---|---|---|---|
所有的变量All variables,r=0.96,p<0.001 | |||||
截距 Intercept | 18.53 | p<0.01 | |||
无霜期FFD | 0.064 | 0.28 | 95.37 | p<0.001 | 91.1 |
年降雨量APP | 0.002 | 0.06 | 18.02 | p<0.001 | 85.2 |
外来游客人数NFT | 3.590 | 0.27 | 6.79 | p<0.05 | 88.1 |
人口密度PLD | -0.479 | -0.26 | 7.12 | p<0.05 | 90.6 |
纬度LTD | -1.440 | -0.58 | 4.44 | p<0.05 | 91.2 |
回归系数 Regression coefficient | 标准化系数 Standardized coefficient | F值 F-value | 显著性水平 Significance | 累积解释方差 Accumulated variance explained (%) | |
---|---|---|---|---|---|
所有的变量All variables,r=0.98,p<0.001 | |||||
截距 Intercept | -4.420 | p<0.05 | |||
交通密度TPD | 0.000 | 0.200 | 123.18 | p<0.001 | 80.41 |
1月平均气温MT1 | 0.057 | 0.398 | 20.59 | p<0.001 | 88.55 |
外来游客人数NFT | -0.320 | -0.286 | 7.50 | p<0.05 | 90.97 |
经度LGD | 0.004 | 0.027 | 5.00 | p<0.05 | 92.39 |
年度生产总值GDP | -0.600 | -0.447 | 1.83 | p<0.05 | 94.49 |
进口货物总额VIC | 0.390 | 0.455 | 3.25 | p<0.05 | 96.00 |
表4 外来入侵植物物种密度和环境因子及人类活动因子的逐步回归
Table 4 Results of stepwise regressions between ID and environmental and anthropological factors
回归系数 Regression coefficient | 标准化系数 Standardized coefficient | F值 F-value | 显著性水平 Significance | 累积解释方差 Accumulated variance explained (%) | |
---|---|---|---|---|---|
所有的变量All variables,r=0.98,p<0.001 | |||||
截距 Intercept | -4.420 | p<0.05 | |||
交通密度TPD | 0.000 | 0.200 | 123.18 | p<0.001 | 80.41 |
1月平均气温MT1 | 0.057 | 0.398 | 20.59 | p<0.001 | 88.55 |
外来游客人数NFT | -0.320 | -0.286 | 7.50 | p<0.05 | 90.97 |
经度LGD | 0.004 | 0.027 | 5.00 | p<0.05 | 92.39 |
年度生产总值GDP | -0.600 | -0.447 | 1.83 | p<0.05 | 94.49 |
进口货物总额VIC | 0.390 | 0.455 | 3.25 | p<0.05 | 96.00 |
图4 中国各省环境和人类活动因子在典范对应分析(CCA)二维轴上的排序图 PAR,LTD,LGD,MT1,MT7,APP,FFD,PLD,TPD,GDP,VIC,NFT,PCA:同表1 See Table 1
Fig.4 CCA ordination for environmental and anthropological factors
[1] | Alpert P, Bone E, Holzapfel C (2000). Invasiveness, invasibility and the role of environmental stress in the spread of non-native plants. Perspectives in Plant Ecology, Evolution and Systematics, 3, 52-66. |
[2] |
Christian CE (2001). Consequences of a biological invasion reveal the importance of mutualism for plant communities. Nature, 413, 635-639.
URL PMID |
[3] | Dark SJ (2004). The biogeography of invasive alien plants in California: an application of GIS and spatial regression analysis. Diversity and Distributions, 10, 1-9. |
[4] | Ehrenfeld JG (2003). Effects of exotic plant invasions on soil nutrient cycling processes. Ecosystems, 6, 503-523. |
[5] | Ehrenfeld JG, Kourtev P, Huang WZ (2001). Changes in soil functions following invasions of exotic understory plants in deciduous forests. Ecological Applications, 11, 1287-1300. |
[6] | Elton CS (1958). The Ecology of Invasions by Animals and Plants. Metheun, London. |
[7] | Fan XH ( 范晓虹), Li WM ( 李尉民) (2001). Research on quarantine strategy for biosafety protection in China. Biodiversity Science (生物多样性), 9, 439-445. (in Chinese with English abstract) |
[8] | Gelbard JL, Belnap J (2003). Roads as conduits for exotic plant invasions in a semiarid landscape. Conservation Biology, 17, 420-432. |
[9] | Gido KB, Schaefer JF, Pigg J (2004). Patterns of fish invasions in the Great Plains of North America. Biological Conservation, 118, 121-131. |
[10] | Higgins SI, Richardson DM, Cowling RM, Trinder-Smith TH (1999). Predicting the landscape-scale distribution of alien plants and their threat to plant diversity. Conservation Biology, 13, 303-313. |
[11] | Hobbs RJ, Huenneke JF (1992). Disturbance, diversity and invasion: implications for conservation. Conservation Biology, 6, 324-337. |
[12] | Hodkinson DJ, Thompson K (1997). Plant dispersal: the role of man. Journal of Applied Ecology, 34, 1484-1496. |
[13] | Hourdequin M (2000). Special section: ecological effects of roads-introduction. Conservation Biology, 14, 16-17. |
[14] | Jenkins PT (1996). Free trade and exotic species introductions. Conservation Biology, 10, 300-302. |
[15] | Levine JM, D'Antonio CM (2003). Forecasting biological invasions with increasing international trade. Conservation Biology, 17, 322-326. |
[16] | Li ZY ( 李振宇), Xie Y ( 谢焱) (2002). Invasive Alien Species in China(中国外来入侵种). China Forestry Publishing House, Beijing. (in Chinese) |
[17] |
Lodge DM (1993). Biological invasions-lessons for ecology. Trends in Ecology & Evolution, 8, 133-137.
DOI URL PMID |
[18] | Lonsdale WM, Lane AM (1994). Tourist vehicles as vectors of weed seeds in Kakadu National Park, Northern Australia. Biological Conservation, 69, 277-283. |
[19] | Ludsin SA, Wolfe AD (2001). Biological invasion theory: Darwin's contributions from The Origin of Species. BioScience, 51, 780-789. |
[20] | Lyons KG, Schwartz MW (2001). Rare species loss alters ecosystem function-invasion resistance. Ecology Letters, 4, 358-365. |
[21] |
Mack MC, D'Antonio CM (1998). Impacts of biological invasions on disturbance regimes. Trends in Ecology & Evolution, 13, 195-198.
URL PMID |
[22] | McKinney CL (2001). Effects of human population, area, and time on non-native plant and fish diversity in the United States. Biological Conservation, 100, 243-252. |
[23] | Mooney HA, Hobbs RJ (2000). Invasive Species in a Changing World. Island Press, Washington, DC. |
[24] | Pimentel D, Lach L, Zuniga R, Morrison D (2000). Environmental and economic costs of nonindigenous species in the United States. BioScience, 50, 53-65. |
[25] | Pimentel D, McNair S, Janecka J, Wightman J, Simmonds C, O'Connell C, Wong E, Russel L, Zern J, Aquino T, Tsomondo T (2001). Economic and environmental threats of alien plant, animal, and microbe invasions. Agriculture Ecosystems & Environment, 84, 1-20. |
[26] | Rohde K (1992). Latitudinal gradients in species-diversity: the search for the primary cause. Oikos, 65, 514-527. |
[27] |
Rose M, Hermanutz L (2004). Are boreal ecosystems susceptible to alien plant invasion? Evidence from protected areas. Oecologia, 139, 467-477.
DOI URL PMID |
[28] | Rouget M, Richardson DM, Nel JL, Le Maitre DC, Egoh B, Mgidi T (2004). Mapping the potential ranges of major plant invaders in South Africa, Lesotho and Swaziland using climatic suitability. Diversity and Distributions, 10, 475-484. |
[29] | Ruiz GM, Carlton JT (2003). Invasive Species: Vectors and Management Strategies. Island Press, Washington. |
[30] | SEPAC ( 国家环境保护总局自然生态保护司) (2002). Nature Reserves in China(全国自然保护区名录). Chinese Environmental Science Press, Beijing. (in Chinese) |
[31] |
Smith MD, Knapp AK (1999). Exotic plant species in a C4-dominated grassland: invasibility, disturbance and community structure. Oecologia, 120, 605-612.
URL PMID |
[32] | Spellerberg IF (1998). Ecological effects of roads and traffic: a literature review. Global Ecology and Biogeography, 7, 317-333. |
[33] | ter Braak CJF (1986). Canonical correspondence analysis: a new eigenvector technique for multivariate direct gradient analysis. Ecology, 67, 1167-1179. |
[34] | Trombulak SC, Frissell CA (2000). Review of ecological effects of roads on terrestrial and aquatic communities. Conservation Biology, 14, 18-30. |
[35] | Tyser RW, Worley CA (1992). Alien flora in grasslands adjacent to road and trail corridors in Glacier National-Park, Montana (USA). Conservation Biology, 6, 253-262. |
[36] | Vila M, Pujadas J (2001). Land-use and socio-economic correlates of plant invasions in European and North African countries. Biological Conservation, 100, 397-401. |
[37] | Vitousek PM, D'Antonio CM, Loope LL, Rejmanek M, Westbrooks R (1997). Introduced species: a significant component of human-caused global change. New Zealand Journal of Ecology, 21, 1-16. |
[38] | Weber E (2001). Current and potential ranges of three exotic goldenrods (Solidago) in Europe. Conservation Biology, 15, 122-128. |
[39] |
Weber EF (1997). The alien flora of Europe: a taxonomic and biogeographic review. Journal of Vegetation Science, 8, 565-572.
DOI URL |
[40] |
Wilcove DS, Rothstein D, Dubow J, Phillips A, Losos E (1998). Quantifying threats to imperiled species in the United States. BioScience, 48, 607-615.
DOI URL |
[41] | Williamson M (1996). Biological Invasions. Chapman and Hall, London. |
[42] | Xie Y, Li ZY, Gregg WP, Li DM (2001). Invasive species in China-an overview. Biodiversity and Conservation, 10, 1317-1341. |
[43] | Zhu DR ( 朱大仁) (2000). Atlas of China(分省中国地图集). China Map Press, Beijing. (in Chinese) |
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