The unintentional transport of species as a result of human activities has reached unprecedented rates. Once established, introduced species can be nearly impossible to eradicate. It is therefore essential to identify and monitor locations where invaders are most likely to establish new populations. Despite the obvious value of early detection, how does an agency identify areas that are most vulnerable to new invaders? Here we propose a novel approach by using the “first detection location” (FDL) of introduced species in China to quantify characteristics of areas where introduced species are first reported.
We obtained FDLs for 166 species (primarily agricultural and forestry pests) that were unintentionally introduced into China prior to 2008 from literature searches. The spatial pattern and determinants of FDLs were examined at the provincial level. The spatial pattern of FDLs varied among provinces with more commerce and trade and economically developed provinces in coastal regions having more FDLs than interior provinces. For example, 74.6% of FDLs were distributed in coastal regions despite that they only cover 15.6% of the total area in China. Variables that may be indicators of “introduction pressure” (e.g. the amount of received commerce) had an overwhelming effect on the number of FDLs in each province (R2 = 0.760).
Our results suggest that “introduction pressure” may be one of the most important factors that determine the locations where newly-introduced species are first detected, and that open and developed provinces in China should be prioritized when developing monitoring programs that focus on locating and managing new introductions. Our study illustrates that FDL approaches can contribute to the study and management of biological invasions not only for China but also for elsewhere.
Citation: Huang D, Zhang R, Kim KC, Suarez AV (2012) Spatial Pattern and Determinants of the First Detection Locations of Invasive Alien Species in Mainland China. PLoS ONE 7(2): e31734. https://doi.org/10.1371/journal.pone.0031734
Editor: Dorian Q. Fuller, University College London, United Kingdom
Received: August 27, 2011; Accepted: January 12, 2012; Published: February 21, 2012
Copyright: © 2012 Huang et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This research was supported by Natural Science Foundation of China program (30525039), Chinese Academy of Sciences program (KSCX2-YW-N-42) and National research programs of China (2005DKA21402/2006FY110500). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Despite considerable prevention efforts, new introductions of alien species continue throughout the world, particularly in areas with high levels of trade and economic development –. Invasive species can be difficult or nearly impossible to eradicate once they have become established in a new area. Therefore, early detection and rapid response (EDRR) is essential for preventing and containing new outbreaks –. Given that increasing levels of international commerce are commonly expected to accelerate the rate at which species are transported , , there is an immediate need to improve the effectiveness of EDRR strategies.
Early detection is inherently difficult as newly introduced species usually occur at low densities , , . High sampling intensity increases the likelihood of successfully detecting rare species . However, a trade-off exists between sampling intensity at any one location and the number of locations searched due to limited resource availability for EDRR efforts . Increasing sampling intensity in areas highly vulnerable to invasion is more effective than searching a wider range with low sampling intensity . Thus, effective EDRR programs that aim at locating and managing newly introduced species will depend on having accurate information on where new species are most likely to become established.
Successful EDRR efforts will also depend upon close collaboration among agencies and organizations at various levels, as new introductions often spread rapidly across jurisdictional boundaries. Thus, the establishment of a national (or even international) EDRR network system may be ideal , . To develop such a system, however, key questions need to be addressed including: (1) where should regional EDRR stations be housed? (2) How should EDRR resources be allocated? (3) What is the geographic distribution of sites where newly introduced species are most likely to become established? The success of EDRR efforts depends upon our capacity to predict potential new introductions across regional scales.
In this study, we use the spatial pattern and abiotic determinants of “first detection locations” (FDLs) of introduced species in mainland China (hereafter termed China) to answer these key questions. We define an FDL as the location where a species of alien origin is detected and identified for the first time in a recipient country or region. FDLs of many alien pests are often reported in or near urban areas and ports of entry. For example, the FDL of Anoplophora glabripennis (Motschulsky) in the United States is in the urban area of New York City . Non-random pattern in the distribution of FDLs can provide crucial information for focusing limited resources for identifying recently established invasive species and guiding EDRR efforts.
Materials and Methods
As the purpose of this study is to develop a dataset of FDLs that may guide strategies for early detection of invasive species, we focus only on species that, (1) are non-native to China, (2) were unintentionally introduced into China, and (3) have been recognized as invasive in the sense that their introduction to China has been accompanied by economic loss, environmental damage and/or harm to human health . Non-native species intentionally introduced into China were not included as the location of their establishment was chosen rather accidental. Species that have been intercepted in imported commerce but have not established in the wild were also excluded. Focusing our efforts on the three criteria above allows us to develop a framework useful for identifying areas where species of the highest concern may become established.
The FDLs of our focal organisms were derived from literature searches, particularly checklists of “invasive alien species” (IAS) in China. We gave priority to the primary literature for reports of the first detection and identification of an IAS, and then used other literature which documented clearly the location where a specific IAS was detected and identified for the first time in China.
Our dataset included FDLs for 166 IASs in China (Table S1). They are mostly agricultural and forestry pests across a wide range of taxa, including plants, insects, fungi, bacteria, and viruses. Thirty-two of these records did not provide detailed information on the exact location of FDL so were excluded from subsequent analyses. The remaining species were divided into three groups: plants, animals and the others (including fungi, bacteria, chromista and virus). The numbers of FDLs of each group in each provincial administrative unit (hereafter termed province) were calculated. As the numbers of FDLs of the three groups in each province were significantly correlated with their pooled data (plants: R = 0.869, P<0.001; animals: R = 0.866, P<001; others: R = 0.608, P<0.001), we used the pooled data to represent the combination of these three groups in the analysis outlined below.
A suite of ecological and socio-economic data by province were collected from publications – and grouped into five categories: (a) introduction pressure, (b) anthropogenic disturbance, (c) search and recording effort, (d) ecological/bio-geographical variability and (e) spread by unintentional introduction (Table 1). Here we used a broad categorization, as some variables could be placed into multiple categories . Introduction pressure (also termed propagule pressure) was used to describe the pressure of a region to receive individuals of alien species .
Spatial pattern of FDLs
To examine the spatial pattern of FDLs at provincial level, we divided provinces in China into three groups according to their geographic positions: coastal regions ( = provinces with sea coasts except Beijing), border regions ( = inland provinces that border other countries) and midland regions (provinces without sea coasts or borders adjacent to other countries) (Fig. 1). Kruskal-Wallis test was used to compare the differences in the number of FDLs in each province among the three regions, as not all these data could be transformed to assume a normal distribution.
Provincial administrative units in mainland China were separated into three groups according to their geographic position: coastal region in blue ( = provinces with sea coasts except Beijing), border region in grey ( = provinces continuous to other countries) and midland region in white ( = provinces without sea coasts or borders on other countries). Bars in red are the number of first detection locations in each province. Bars in yellow and green (for the average GDP and import value of commodities from 1986 to 2007, respectively) are standardized with same height in Guangdong province which has the highest GDP and the highest number of first detection locations. AH, BJ, CQ, FJ, GS, GD, GX, GZ, HeB, HeN, HLJ, HN, HuB, HuN, JL, JS, JX, NMG, NX, QH, SD, SaX, SaaX, SC, SH, TJ, XJ, XZ, YN and ZJ are provinces codes, standing for Anhui, Beijing, Chongqing, Fujian, Gansu, Guangdong, Guangxi, Guizhou, Hebei, Henan, Heilongjiang, Hainan, Hubei, Hunan, Jilin, Jiangsu, Jiangxi, Inner Mongolia, Ningxia, Qinghai, Shandong, Shanxi, Shaanxi, Sichuan, Shanghai, Tianjin, Xinjiang, Tibet, Yunnan and Zhejiang, respectively.
Determinants of FDL distribution
Spearman rank correlation was used to identify potential relationships between variables used in this study. As many explanatory variables were highly interrelated (Table S2), and relationships between these variables may be strongly nonlinear and involve high-order interactions, we built regression trees – to explain the spatial pattern of FDLs. The trees were built by repeatedly splitting the response variable (i.e. the number of FDLs in each province) using binary recursive partitioning in CART v. 6.0.
To find the best tree, 50 sets of 10-fold cross-validation were run, on the basis of the minimum cost tree rule, which minimizes the cross-validated relative error, and on the one-SE rule, which minimizes cross-validated relative error within one SE of the minimum, respectively . The most frequent (most likely) single tree was chosen for description. Ten-fold cross-validation was used to estimate the cross-validated relative error and resubstituion relative error of this tree. Total variance of response variable explained by the best tree was calculated as R2 = 1−resubstitution relative error. The quality of each split was corresponding to proportion of the total sum of squares explained by the tree at each node.
The distribution of FDLs varied among provinces with more commerce and trade and economically developed provinces in coast regions having more FDLs than provinces in border and midland regions (Fig. 1). For example, the number of FDLs was highest in Guangdong, a coastal province (17), whereas its neighbor Hunan Province, a midland province had only one. By comparison, Hunan is 0.2 times larger than Guangdong but only produces 33.4% and 1.5% of Guangdong's GDP and import value (respectively). FDLs were mostly (74.6% of the total) distributed in coastal regions which occupied only 15.6% of the total land area of China. The mean number of FDLs per province in coastal region was 8.3±1.4 (mean ± SE), 1.2 times higher than that in border region (3.7±1.5) and 8.2 times higher than that in midland region (0.9±0.3). Kruskal-Wallis test showed their difference was significant (χ2 = 16.565, P<0.000). These results indicated that IASs were more likely detected first in coastal region compared to border or midland regions.
The number of FDLs in each province was significantly related to variables that may be indicators of introduction pressure (e.g. the number of water ports of entry, the number of international tourists) and variables that reflect human disturbance on recipient regions (e.g. population density, gross domestic product per capita per capita) (Table S2).
Regression trees further support this pattern. When all explanatory variables were included, the cross-validated relative error of the best tree was 0.563, indicating that this model had predictive capacity of the FDL distribution. The tree explained 86.1% of variance, of which 76.0% was attributed to two variables that represent introduction pressure, and 10.1% to funds for scientific research that reflects search and recording effort (Fig. 2 A). As variables of other categories (e.g., gross domestic product per capita) were important and strong competitors of the first splitter (Table S3), we removed all variables of the “IP” category (Table 1) to explore whether the effects of other factors were masked ((or “squeezed out”)) by variables representing introduction pressure. The cross-validated relative error of the resulting best tree was 0.717. It had only two terminal nodes, split by gross domestic product per capita that explained 46.4% of variance (Fig. 2 B). No other predictive trees were constructed (i.e. cross-validated relative error >1.0), when we removed all variables of the “IP” and “DI, IP” categories.
A: using all explanatory variables; B: using explanatory variables except those classified into “IP” category (Table 1). Each node of the tree is described by the splitting variable, its splitting criteria, percentage of variance the splitter explains, mean ± standard deviation for the number of first detection locations of invasive alien species, and the number of sample (i.e. species) at that node in brackets. (Inset) Cross-validation processes for selection of the best regression trees. Line shows a single representative 10-fold cross-validation of the most frequent (modal) best trees with standard error (SE) estimates of each tree size. Bar charts are the numbers of the optimal trees of each size (frequency of tree) selected from a series of 50 cross-validations based on the minimum cost tree, which minimizes the cross-validated relative error (white, SE rule 0), and 50 cross-validations based on the one-SE rule (gray, SE rule 1), which minimizes the cross-validated relative error within one SE of the minimum. The most frequent trees have four terminal nodes. See the legend of Fig. 1 for province codes.
Species number and available data
Compiling a list of IASs for a given recipient region is a helpful approach to understand patterns of invasion . Because we focused only on the species that were unintentionally introduced into and have evidently done damage in China, our species list certainly represents only a fraction of all alien species in China. Having a list of all alien species and their FDLs would be indispensable, but is presently not feasible to obtain. This reflects a knowledge gap that needs to be filled and also the difficulty in collecting accurate FDLs for species once they have been established for a long period of time. As is the case in many countries, there is currently no central repository for records of invasive species in China.
While our species list is incomplete, it is likely representative of the larger species pool of IASs that were unintentionally introduced into China. The number of IASs in China is currently unknown although a checklist published in 2004 listed 283 species (including intentionally and unintentionally introduced IASs, and those that naturally dispersed into China), a likely underestimate , . For example, previous checklists ,  do not include invaders discovered in recent years, such as Solenopsis invicta Buren and Phenacoccus solenopsis Tinsley. Nascent lists may have a larger number of IASs –. However, they include species native to China, such as Coptotermes formosanus Shiraki that become alien and invasive out of their native range within China, and contain those that have been intercepted but not yet established in China, such as Anthonomus grandis (Boheman). Future efforts will benefit from drawing upon both a larger data set of species and also from including more regions either nationally or internationally.
FDL spatial distribution
Our results suggest that IASs unintentionally introduced into China were more frequently first detected in coastal provinces. This pattern is similar to those revealed in previous studies , , , showing that the numbers of IASs in coastal provinces are higher than those in inland provinces. However, previous results find the distribution pattern of introduced species to be correlated significantly with domestic traffic and climate, and strongly associated with economic development but weakly with international transport . In contrast, our results strongly implicated international transport and other forms of “propagule pressure” (Fig. 2 A, Table S2).
It is important to note that many our focal IASs, such as Liriomyza sativae Blanchard and Lissorhoptrus oryzophilus Kuschel, have invaded midland provinces. However, few were first detected in this region , , . One possible explanation to these contrasting patterns could be due to patterns of spread; IASs entering midland regions may be detected after spreading from coastal provinces rather than the reverse. Support for this may come from the fact that variables representing spread by domestic transport were weakly correlated with the number of FDLs in each province (Table S2) and explained little of the variance in the number of FDLs (not appeared in the optimal trees, Fig. 2 A).
In our view, a more reasonable explanation could be that most IASs found in midland provinces spread from frontier provinces, and most IASs initially entering coastal provinces were discovered prior to their detections in midland provinces, as coastal regions had much higher introduction pressure (with 91.0% of the total import value, 78.6% of the total international tourists in China), which accounted for most of the variance that was much higher than those explained by other factors (Fig. 2 A). This concurs with previous studies suggesting that a booming economy sparks and accelerates biological invasions in China , .
Factors that affect FDL distribution
Theoretically, FDLs may be determined by many factors including international transport, domestic traffic, biological traits of species, native biodiversity, climatic suitability, and search and recording effort. In comparison to these latent factors, our results appeared somewhat unexpected. These variables were weakly related with our response variable (Table S2), and did not appear in the best regression trees (Fig. 2 A, B). This does not mean that those factors have no roles in the FDL distribution. They may affect the FDL distribution at larger or lower scales.
Our study showed an overwhelming effect of variables representing introduction pressure on the number of FDLs in each province (Table S2, Fig. 2 A), indicating that introduction pressure is one of the most important determinants on the FDL distribution. This result is in agreement with a commonly accepted paradigm that international transport plays an important role in the spread of IASs –.
Significant associations of the number of FDLs in each province with population density (Table S2) and the presence of funds for scientific research in the regression tree (Fig. 2 A) suggest that search and recording effort may be an important determinant of where introduced species are first detected. This has been demonstrated in many IASs such as S. invicta  and Bursaphelenchus xylophilus (Steiner and Buhre) , which were first discovered in areas where people were already aware of their potential presence and hazards before first detection.
High degree of disturbance can increase the vulnerability of recipient ecosystems . This favorable factor could lead to an increase of species relative abundance, which is an important determinant of the discovery of introduced species . Our study revealed that variables such as gross domestic product per capita, urbanization rate that may be indicators of disturbance  were significantly related with the number of FDLs. Also, gross domestic product per capita was the third strongest competitor of the first splitter of the best regression tree (Fig. 2 A, Table S3) and explained a considerable fraction of the variance in the number of FDLs (Fig. 2 B). These results suggest that disturbance may be another important determinant of the FDL distribution.
Implications for managing new introductions
As the international transport between China and other regions continues to grow, the number of new introductions will increase. Many species listed in the Global Invasive Species Database are posing potential threats to China . The patterns revealed in our study can be useful in developing programs that aim at locating and managing new introductions. For example, when designing a national EDRR network system, regional stations should be prioritized in coastal and developed provinces. It is particularly worth directing more EDRR resources to Bohai Rim, Yangtze River Delta and Pearl River Delta, because these areas are widely open, highly developed and disturbed in China.
The differences between present distribution pattern and first detection pattern show that domestic transport may have accelerated the spread of IASs in China . This highlights the importance of post-border inspection and interception that aim to reduce the unintentional introductions between provinces.
Expanding this approach to other scales
Here we provided a case study to illustrate how FDL approach can contribute to the study of biological invasions. This approach can be expanded at both larger and smaller scales. At global scale, more variables can be investigated and their relative importance assessed. For example, across continents the relative importance of commerce can be compared to abiotic variables. Biological invasions are conceptually considered depending on propagule pressure and abiotic suitability . Their relative importance in the determination of establishment success may be estimated by this approach. At national scale, we can compare the similarity and differences of the distribution patterns of FDLs in various countries to find common patterns and rules. At landscape scale, we can quantify the habitat type and ecosystem type of the FDLs and better understand their relationships with the biological traits of IASs.
List of invasive alien species and their first detection locations in mainland China.
Full Spearman rank correlation matrix of all variables used in this study.
We thank Zhimin Su for assistance in the FDL data collection, thank Yingchao Li as well as all other members of the research group of Identification & Management of Invasive Alien Insects in the Institute of Zoology, CAS for helps during the research, thank John M. Randall, Richard B. Primack and Minsheng You for valuable suggestions on earlier manuscripts, and thank Jane Catherine Stout and two anonymous reviewers for critical comments on the manuscript.
Conceived and designed the experiments: DH RZ. Performed the experiments: DH. Analyzed the data: DH. Contributed reagents/materials/analysis tools: DH. Wrote the paper: DH RZ KCK AVS.
- 1. Lin W, Zhou G, Cheng X, Xu R (2007) Fast economic development accelerates biological invasions in China. PLoS ONE 2: e1208.W. LinG. ZhouX. ChengR. Xu2007Fast economic development accelerates biological invasions in China.PLoS ONE2e1208
- 2. Hulme PE (2009) Trade, transport and trouble: managing invasive species pathways in an era of globalization. J Appl Ecol 46: 10–18.PE Hulme2009Trade, transport and trouble: managing invasive species pathways in an era of globalization.J Appl Ecol461018
- 3. DAISIE (2008) Handbook of Alien Species in Europe. Berlin: Springer. 399 p.DAISIE2008Handbook of Alien Species in EuropeBerlinSpringer399
- 4. Jeschke JM, Strayer DL (2005) Invasion success of vertebrates in Europe and North America. P Natl Acad Sci USA 102: 7198–7202.JM JeschkeDL Strayer2005Invasion success of vertebrates in Europe and North America.P Natl Acad Sci USA10271987202
- 5. Cohen AN, Carlton JT (1998) Accelerating invasion rate in a highly invaded estuary. Science 279: 555–558.AN CohenJT Carlton1998Accelerating invasion rate in a highly invaded estuary.Science279555558
- 6. Richardson DM, Pyšek P (2008) Fifty years of invasion ecology: the legacy of Charles Elton. Divers Distrib 14: 161–168.DM RichardsonP. Pyšek2008Fifty years of invasion ecology: the legacy of Charles Elton.Divers Distrib14161168
- 7. Hulme PE (2006) Beyond control: wider implications for the management of biological invasions. J Appl Ecol 43: 835–847.PE Hulme2006Beyond control: wider implications for the management of biological invasions.J Appl Ecol43835847
- 8. Genovesi P (2005) Eradications of invasive alien species in Europe: a review. Biol Invasions 7: 127–133.P. Genovesi2005Eradications of invasive alien species in Europe: a review.Biol Invasions7127133
- 9. Mehta SV, Haight RG, Homans FR, Polasky S, Venette RC (2007) Optimal detection and control strategies for invasive species management. Ecol Econ 61: 237–245.SV MehtaRG HaightFR HomansS. PolaskyRC Venette2007Optimal detection and control strategies for invasive species management.Ecol Econ61237245
- 10. Levine JM, D'Antonio CM (2003) Forecasting biological invasions with increasing international trade. Conserv Biol 17: 322–326.JM LevineCM D'Antonio2003Forecasting biological invasions with increasing international trade.Conserv Biol17322326
- 11. Westphal M, Browne M, MacKinnon K, Noble I (2008) The link between international trade and the global distribution of invasive alien species. Biol Invasions 10: 391–398.M. WestphalM. BrowneK. MacKinnonI. Noble2008The link between international trade and the global distribution of invasive alien species.Biol Invasions10391398
- 12. Meentemeyer RK, Anacker BL, Mark W, Rizzo DM (2008) Early detection of emerging forest disease using dispersal estimation and ecological niche modeling. Ecol Appl 18: 377–390.RK MeentemeyerBL AnackerW. MarkDM Rizzo2008Early detection of emerging forest disease using dispersal estimation and ecological niche modeling.Ecol Appl18377390
- 13. Gotelli NJ, Colwell RK (2001) Quantifying biodiversity: procedures and pitfalls in the measurement and comparison of species richness. Ecol Lett 4: 379–391.NJ GotelliRK Colwell2001Quantifying biodiversity: procedures and pitfalls in the measurement and comparison of species richness.Ecol Lett4379391
- 14. Venette RC, Moon RD, Hutchison WD (2002) Strategies and statistics of sampling for rare individuals. Ann Rev Entomol 47: 143–174.RC VenetteRD MoonWD Hutchison2002Strategies and statistics of sampling for rare individuals.Ann Rev Entomol47143174
- 15. Harvey CT, Qureshi SA, MacIsaac HJ (2009) Detection of a colonizing, aquatic, non-indigenous species. Divers Distrib 15: 429–437.CT HarveySA QureshiHJ MacIsaac2009Detection of a colonizing, aquatic, non-indigenous species.Divers Distrib15429437
- 16. National Invasive Species Council (2008) National Invasive Species Council20082008–2012 National Invasive Species Management Plan: Available from http://www.invasivespecies.gov/main_nav/mn_NISC_ManagementPlan.html. Accessed 2011 Mar 15. 2008–2012 National Invasive Species Management Plan: Available from http://www.invasivespecies.gov/main_nav/mn_NISC_ManagementPlan.html. Accessed 2011 Mar 15.
- 17. Genovesi P, Shine C (2003) European Strategy on Invasive Alien Species: Council of Europe, Strasbourg. P. GenovesiC. Shine2003European Strategy on Invasive Alien Species: Council of Europe, Strasbourg.T-pvs (2003) 7 revised. T-pvs (2003) 7 revised.
- 18. Haack RA, Law KR, Mastro VC, Ossenbruggen HS, Raimo BJ (1997) New York's battle with the Asian long-horned beetle. J Forest 95: 11–15.RA HaackKR LawVC MastroHS OssenbruggenBJ Raimo1997New York's battle with the Asian long-horned beetle.J Forest951115
- 19. McNeely JA, Mooney HA, Neville LE, Schei PJ, Waage JK (2001) JA McNeelyHA MooneyLE NevillePJ ScheiJK Waage2001A Global Strategy on Invasive Alien Species: IUCN Gland, Switzerland, and Cambridge, UK. A Global Strategy on Invasive Alien Species: IUCN Gland, Switzerland, and Cambridge, UK.
- 20. National Bureau of Statistics of China (1986) China Statistical Yearbook. Beijing: China Statistics Press. National Bureau of Statistics of China1986China Statistical YearbookBeijingChina Statistics Press
- 21. China Association of Port-of-Entry (2003) Practical manual of ports of entry in China. Beijing: China Customs Press. China Association of Port-of-Entry2003Practical manual of ports of entry in ChinaBeijingChina Customs Press
- 22. McBeath GA, Leng T (2006) Governance of Biodiversity Conservation in China and Taiwan. Cheltenham, UK and Northampton, MA, USA: Edward Elgar. GA McBeathT. Leng2006Governance of Biodiversity Conservation in China and TaiwanCheltenham, UK and Northampton, MA, USAEdward Elgar
- 23. Lockwood JL, Cassey P, Blackburn T (2005) The role of propagule pressure in explaining species invasions. Trends Ecol Evol 20: 223–228.JL LockwoodP. CasseyT. Blackburn2005The role of propagule pressure in explaining species invasions.Trends Ecol Evol20223228
- 24. Breiman L, Friedman J, Olshen R, Stone C (1984) Classification and Regression Trees. Pacific Grove: Wadsworth. L. BreimanJ. FriedmanR. OlshenC. Stone1984Classification and Regression TreesPacific GroveWadsworth
- 25. Steinberg G, Colla P (1995) Tree-Structured Non-Parametric Data Analysis. San Diego: Salford Systems. G. SteinbergP. Colla1995Tree-Structured Non-Parametric Data AnalysisSan DiegoSalford Systems
- 26. De'Ath G, Fabricius KE (2000) Classification and regression trees: a powerful yet simple technique for ecological data analysis. Ecology 81: 3178–3192.G. De'AthKE Fabricius2000Classification and regression trees: a powerful yet simple technique for ecological data analysis.Ecology8131783192
- 27. Weber E, Sun S, Li B (2008) Invasive alien plants in China: diversity and ecological insights. Biol Invasions 10: 1411–1429.E. WeberS. SunB. Li2008Invasive alien plants in China: diversity and ecological insights.Biol Invasions1014111429
- 28. Xu H, Qiang S, Han Z, Guo J, Huang Z, et al. (2006) The status and causes of alien species invasion in China. Biodivers Conserv 15: 2893–2904.H. XuS. QiangZ. HanJ. GuoZ. Huang2006The status and causes of alien species invasion in China.Biodivers Conserv1528932904
- 29. Xu H, Qiang S, Han Z, Guo J, Huang Z, et al. (2004) The distribution and introduction pathway of alien invasive species in China. Biodivers Sci 12: 626–638.H. XuS. QiangZ. HanJ. GuoZ. Huang2004The distribution and introduction pathway of alien invasive species in China.Biodivers Sci12626638
- 30. Xu H, Qiang S (2004) Checklist of invasive alien species in China. Beijing: China Environmental Science Press. 432 p.H. XuS. Qiang2004Checklist of invasive alien species in ChinaBeijingChina Environmental Science Press432
- 31. Li Z, Xie Y (2002) Invasive Alien Species in China. Beijing: China Forestry Publishing House. 211 p.Z. LiY. Xie2002Invasive Alien Species in ChinaBeijingChina Forestry Publishing House211
- 32. Xie Y (2008) Bioinvasion and Ecological Security in China. Shijiazhuang: Hebei Science and Technology Publishing House. 696 p.Y. Xie2008Bioinvasion and Ecological Security in ChinaShijiazhuangHebei Science and Technology Publishing House696
- 33. Wan F, Zheng X, Guo J (2005) Biology and management of invasive alien species in agriculture and forestry. Beijing: Science Press. 820 p.F. WanX. ZhengJ. Guo2005Biology and management of invasive alien species in agriculture and forestryBeijingScience Press820
- 34. Wan F, Xie B, Chu D (2008) Biological Invasions, legislations and management stratagies. Beijing: Science Press. 316 p.F. WanB. XieD. Chu2008Biological Invasions, legislations and management stratagiesBeijingScience Press316
- 35. Wu S, Sun H, Teng Y, Rejmánek M, Chaw S, et al. (2010) Patterns of plant invasions in China: Taxonomic, biogeographic, climatic approaches and anthropogenic effects. Biol Invasions 12: 2179–2206.S. WuH. SunY. TengM. RejmánekS. Chaw2010Patterns of plant invasions in China: Taxonomic, biogeographic, climatic approaches and anthropogenic effects.Biol Invasions1221792206
- 36. Liu J, Liang S, Liu F, Wang R, Dong M (2005) Invasive alien plant species in China: regional distribution patterns. Divers Distrib 11: 341–347.J. LiuS. LiangF. LiuR. WangM. Dong2005Invasive alien plant species in China: regional distribution patterns.Divers Distrib11341347
- 37. Wan F, Guo J, Zhang F (2009) Research on Biological Invasions in China. Beijing: Science Press. 302 p.F. WanJ. GuoF. Zhang2009Research on Biological Invasions in ChinaBeijingScience Press302
- 38. Ding J, Mack RN, Lu P, Ren M, Huang H (2008) China's booming economy is sparking and accelerating biological invasions. Bioscience 58: 317–324.J. DingRN MackP. LuM. RenH. Huang2008China's booming economy is sparking and accelerating biological invasions.Bioscience58317324
- 39. Vitousek PM, D'Antonio CM, Loope LL, Rejmanek M, Westbrooks R (1997) Introduced species: a significant component of human-caused global change. New Zeal J Ecol 21: 1–16.PM VitousekCM D'AntonioLL LoopeM. RejmanekR. Westbrooks1997Introduced species: a significant component of human-caused global change.New Zeal J Ecol21116
- 40. Lockwood JL, McKinney ML (2001) Biotic homogenization. New York: Kluwer Academic/Plenum Publishers. 292 p.JL LockwoodML McKinney2001Biotic homogenizationNew YorkKluwer Academic/Plenum Publishers292
- 41. Wheeler AG, Hoebeke ER (2009) Adventive (non-native) insects: importance to science and society. In: Foottit RG, Adler PH, editors. Insect Biodiversity: Science and Society: Wiley-Blackwell. pp. 475–521.AG WheelerER Hoebeke2009Adventive (non-native) insects: importance to science and society.RG FoottitPH AdlerInsect Biodiversity: Science and Society: Wiley-Blackwell475521
- 42. Zeng L, Lu Y, He X, Zhang W, Liang G (2005) Identification of red imported fire ant Solenopsis invicta to invade mainland China and infestation in Wuchuan, Guangdong. Chin Bull Entomol 42: 144–148.L. ZengY. LuX. HeW. ZhangG. Liang2005Identification of red imported fire ant Solenopsis invicta to invade mainland China and infestation in Wuchuan, Guangdong.Chin Bull Entomol42144148
- 43. Sun Y (1982) The pine wilt nematode (Bursaphelenchus xylophilus) detected at Sun Yet-sen's mausoleum in Nanjing. J Jiangsu Forest Sci Tech 9: 47.Y. Sun1982The pine wilt nematode (Bursaphelenchus xylophilus) detected at Sun Yet-sen's mausoleum in Nanjing.J Jiangsu Forest Sci Tech947
- 44. Alpert P, Bone E, Holzapfel C (2000) Invasiveness, invasibility and the role of environmental stress in the spread of non-native plants. Perspect Plant Ecol Evol Syst 3: 52–66.P. AlpertE. BoneC. Holzapfel2000Invasiveness, invasibility and the role of environmental stress in the spread of non-native plants.Perspect Plant Ecol Evol Syst35266
- 45. Costello CJ, Solow AR (2003) On the pattern of discovery of introduced species. P Natl Acad Sci USA 100: 3321–3323.CJ CostelloAR Solow2003On the pattern of discovery of introduced species.P Natl Acad Sci USA10033213323
- 46. Zhang R, Zhang Y, Jiang Y (2008) Threats of global invasive alien insects to China. Sci Chin Ser C-Life Sci 38: 1095–1102.R. ZhangY. ZhangY. Jiang2008Threats of global invasive alien insects to China.Sci Chin Ser C-Life Sci3810951102
- 47. Leung B, Mandrak NE (2007) The risk of establishment of aquatic invasive species: joining invasibility and propagule pressure. P Roy Soc B-Biol Sci 274: 2603–2609.B. LeungNE Mandrak2007The risk of establishment of aquatic invasive species: joining invasibility and propagule pressure.P Roy Soc B-Biol Sci27426032609