ABSTRACT
Invasive species have attracted widespread attention because of their ecological, economic, and social impacts. Vernonia amygdalina Del. (commonly known as bitter leaf) is a perennial shrub in the Asteraceae family, native to tropical Africa and widely recognized for its medicinal value. In recent years, this species has been reported sporadically in southern China, raising concerns about its potential to become invasive. Here, we assess the risk of invasion posed by V. amygdalina through synthesizing evidence on its taxonomic background, morphological and life‐history traits, reproductive strategies, allelopathic effects, defense mechanisms, climate suitability, and human‐mediated introduction and cultivation practices. Overall, the available evidence suggests that V. amygdalina may have substantial invasion potential, supported by high reproductive capacity, strong allelopathic effects, effective defense traits, and broad climatic tolerance. Moreover, current introduction and cultivation practices in southern China may further increase invasion risk by elevating propagule pressure. Preventive actions, including early detection, targeted monitoring, and surveillance systems will be important for managing this species and mitigating potential ecological threats. Our synthesis also highlights the value of assessing invasion risk before introducing non‐native species.
Keywords: allelopathy, Asteraceae, invasive species, Vernonia amygdalina
This study evaluates the invasion potential of Vernonia amygdalina by synthesizing evidence on its taxonomic background, morphological and life‐history traits, reproductive strategies, allelopathic effects, defense mechanisms, climatic suitability, and human‐mediated introduction and cultivation practices. Overall, the evidence suggests that V. amygdalina may have substantial invasion potential, supported by high reproductive capacity, pronounced allelopathic effects, effective defense traits, and broad climatic tolerance.

1. Introduction
Invasive species are major drivers of global ecosystem change and have received increasing attention (Devenish et al. 2024; Holdrege et al. 2024; Rodrigues et al. 2024), underscoring the need to advance research on invasion mechanisms and control strategies. Studies of biological invasions generally focus on three core components: (i) the invasive potential of species, (ii) the invasibility of recipient environments, and (iii) effective control measures. Environmental invasibility refers to the susceptibility of a habitat to invasion. It is shaped by climate suitability, resource availability, disturbance regimes, and human‐mediated habitat modification, all of which can facilitate the establishment and spread of alien species (Davis et al. 2000; Shea and Chesson 2002). Control measures aim to prevent or limit invasion through early warning, targeted monitoring, and rapid response (e.g., containment or eradication at the incipient stage), thereby reducing ecological impacts and the long‐term management costs (Reaser et al. 2020; Heimovitz et al. 2024). Assessing a species' likelihood of becoming invasive is a prerequisite and a central focus of invasion research, providing essential guidance for management and monitoring strategies (Antunes and Schamp 2017).
Invasive species originate outside their introduced ranges and enter new environments through nonnatural pathways, primarily via human activities, and they can exert substantial negative impacts on native ecosystems (Khatri et al. 2025a; Negi et al. 2025). Once established, they can self‐reproduce and cause ecological, social, and economic harm (Li et al. 2001; Li and Chen 2002). Many invasive plants show vigorous growth and competitive dominance in novel environments (Khatri et al. 2022). Among major threats to global biodiversity, biological invasions rank second only to habitat destruction (Fartyal et al. 2025). In recent decades, international trade and human mobility have accelerated both intentional and accidental introductions of plant species across regions (Negi et al. 2023), contributing to the escalating global invasion problem (Seebens et al. 2017; Khatri et al. 2023). Importantly, not all exotic species become invasive; therefore, evaluating the invasion potential of non‐native species is critical for identifying those that may pose future risks (Li et al. 2001).
Furthermore, China is among the countries most severely affected by biological invasions (Turbelin et al. 2024). Since the 1980s, China has conducted risk assessments for alien species, including evaluating quarantine significance for harmful pests and weeds (Fan and Zhao 1997; Li and Xie 2002). Risk‐assessment systems for invasive species have since been continually refined (Hao et al. 2011; Wan et al. 2017; Zheng et al. 2024). Nevertheless, limitations—including incomplete information on species, insufficient suitability analyses, and challenges in ensuring objectivity—have constrained broad application of these frameworks (Li et al. 2022). Because many traits relevant to invasiveness are difficult to quantify, predicting whether an alien species will become invasive remains challenging. Beyond intrinsic species traits, environmental invasibility and anthropogenic factors often play key roles (Weber and Li 2008). For example, Gao et al. (2018) summarized general patterns of invasive plants in China and the United States by analyzing taxonomic, morphological, and reproductive traits, invasion history, native‐range information, and human influence. Integrating such general invasion‐related traits to evaluate specific non‐native species can support early warning and proactive management (Pfadenhauer and Bradley 2024; Pili et al. 2024).
Building on this framework, we assessed the invasive potential of Vernonia amygdalina Del., an alien species that is currently sparsely distributed in southern China (Figure 1). We synthesized available evidence on its invasion‐related traits. Our aim is to develop a conceptual framework for evaluating the invasion potential of alien species. V. amygdalina is a perennial shrub or small tree in the Asteraceae family, native to tropical Africa. It has recognized medicinal value in traditional medicine (Alebie et al. 2017) and is widely cultivated in many regions worldwide. In recent years, it has been reported sporadically occurring in southern China (Liu et al. 2022). Based on our review of its traits—particularly taxonomy, distribution, reproductive biology, and potential allelopathic effects—we suggest that V. amygdalina may pose a non‐negligible invasion risk in China. This assessment is framed by three working hypotheses: (1) Reproduction hypothesis: V. amygdalina may establish and spread readily because it can reproduce efficiently via both seeds and root sprouting. (2) Climate suitability hypothesis: under suitable climatic conditions, V. amygdalina may show higher survival and faster expansion. (3) Competitive/allelopathy hypothesis: V. amygdalina may gain an advantage over nearby native plants, potentially through allelopathic effects. Overall, this review evaluates the invasion potential of V. amygdalina from the perspectives of taxonomy, morphology, reproduction, allelopathy, and defense mechanisms, with the goal of providing early warning of the invasion risk posed by this alien species.
FIGURE 1.

Wild individuals of Vernonia amygdalina observed on the campus of South China Normal University (A) and the South China National Botanical Garden (B). The species is capable of natural regeneration and local spread under field conditions; mature plants typically reach ~2–5 m in height. Photographs were taken by the authors.
Because explicit studies evaluating the invasiveness of V. amygdalina remain scarce—whereas most published work emphasizes its medicinal or forage value—a formal meta‐analysis is not currently feasible. We therefore adopt a qualitative, trait‐based evidence synthesis by systematically collating information from the available literature and complementing it with occurrence records from the Global Biodiversity Information Facility (GBIF) to summarize its distribution pattern. Given the limited number of studies directly testing allelopathy in V. amygdalina, we also include a simple seed‐germination bioassay in the allelopathy section to provide empirical support for potential inhibitory effects.
2. Taxonomic Characteristics of V. amygdalina
Vernonia amygdalina belongs to the Asteraceae, one of the largest families of flowering plants and frequently reported among alien and invasive floras. Most Asteraceae species are herbaceous plants, subshrubs, or shrubs, with relatively few tree species. An analysis of the taxonomic traits of invasive plants in China revealed that Asteraceae constitutes a significant proportion of the country's invasive flora, accounting for 23% of invasive species (Gao et al. 2018). Many of the most common invasive species in China belong to this family, including Solidago canadensis L., Pluchea indica (L.) Less., Eupatorium adenophorum Spreng, Eupatorium odoratum L., Bidens pilosa L., and Sphagneticola trilobata (L.) Pruski (Gao et al. 2018).
The invasive species from the family Asteraceae are often characterized by their strong invasiveness and destructive impacts, attracting considerable attention. For instance, Yang et al. (2023) studied 33 invasive Asteraceae plants in China and found that, under current climatic conditions, their potential distribution is primarily concentrated in southeastern China. Many Asteraceae are fast‐growing and produce capitulum inflorescences with numerous small seeds, typically bearing a pappus that facilitates wind dispersal. In addition, allelopathy is common in the family. Together, these traits contribute to the prominence of Asteraceae among invasive plants worldwide. Accordingly, the appearance of alien Asteraceae species in a region warrants heightened vigilance and proactive risk assessment (Yang et al. 2023).
3. Morphological Characteristics
In contrast to many other Asteraceae species, V. amygdalina is primarily a shrub or small tree, typically 2–5 m tall and occasionally reaching 10 m (Ijeh and Ejike 2011; Houegban et al. 2024). It has a well‐developed root system that is drought‐tolerant and adaptable to a range of soil conditions (Bonsi et al. 1995; Kaur et al. 2019). Roots can sprout upright shoots, enabling clonal propagation (Bonsi et al. 1995).
The bark of V. amygdalina is rough, and its stems are robust and highly lignified, providing strong structural support. Stem epidermal cells have thick cell walls and a well‐developed cuticle, which reduces water loss and may facilitate persistence in relatively dry environments (Bonsi et al. 1995).
Capitulum inflorescences are borne terminally or in axils and can produce seeds. The fruit is an achene, cylindrical to top‐shaped with ribs, with a truncate apex often accompanied by callus tissue at the base. Achenes may be short‐haired or glabrous and can sometimes be glandular. The pappus is usually two‐layered, though occasionally single‐layered: the inner layer is elongated and bristle‐like (deciduous or persistent), whereas the outer layer is short, consisting of many or few bristles or scales, and may be absent.
Seeds are small and abundant, conferring high reproductive capacity. Under suitable conditions, this can facilitate rapid dispersal and establishment. Achenes may be dispersed by wind, water, and animals. Seed dispersal efficiency is closely linked to spread, and invasive species often exhibit high dispersal efficiency (Teller et al. 2016; Martín‐Forés et al. 2018). Among dispersal modes, wind dispersal is especially effective (Teller et al. 2016). Work on common invasive Asteraceae in Yunnan, China, shows that dispersal distance is positively related to seed size and pappus traits (Peng et al. 2018). Thus, the small, abundant seeds of V. amygdalina, coupled with pappus structures, likely enhance its potential for rapid spread and successful establishment.
4. Reproductive Characteristics
The reproductive strategies of V. amygdalina are diverse and efficient (Houegban et al. 2024). Its well‐developed root system can produce upright shoots, and field observations suggest it can propagate clonally in the wild (Houegban et al. 2024), potentially forming monoclonal patches. Clonal reproduction is common among invasive plants; for example, 37% of invasive species in the wild rely predominantly on clonal reproduction (Gao et al. 2018). Clonal modes include root sprouting, adventitious roots, stolons, and even propagation via leaves or axillary buds (Gao et al. 2018).
Clonal reproduction can enable rapid occupation of available habitat and secure access to resources. Increases in clonal ramets may also enhance pollen availability, thereby improving sexual reproductive success (Buchanan 2015). Consequently, clonal growth can facilitate successful sexual reproduction (Herrera and Nassar 2009; Mariani et al. 2010; Semizer‐Cuming et al. 2019).
For V. amygdalina, sexual reproduction appears to be the primary mode of propagation. Individuals can flower and set seed within the same year. In Africa, seed propagation is the main method used in cultivation (Houegban et al. 2024). Under natural conditions, seeds typically germinate within 2–4 weeks. During the flowering season, individuals can produce large numbers of seeds, potentially allowing rapid occupation of a habitat within a few years after introduction.
5. Allelopathic Effects
Allelopathy is widely recognized as a mechanism that can enhance plant competitiveness (Bieberich et al. 2018; Wang et al. 2024; Joshi et al. 2025; Khatri et al. 2025b), and is often framed as a “novel weapon” in plant invasions (Svensson et al. 2013; Zheng et al. 2015; Qi et al. 2020). Trait compilations indicate that 52% of invasive species in China and 36% in the United States show allelopathic capacity (Gao et al. 2018). Many invasive plants release secondary metabolites (e.g., phenolics) into the surrounding environment via leaching, volatilization, and other pathways. These compounds can inhibit germination and growth of neighboring plants and thereby reduce their competitiveness (Kim and Lee 2011; Al Harun et al. 2014; Kato‐Noguchi and Kurniadie 2022).
Allelopathic effects can reduce seed germination of native plants and ultimately lower local biodiversity (Kim and Lee 2011). Leaves of V. amygdalina contain abundant phenolic compounds (Farombi and Owoeye 2011). In other systems, strong allelopathy has been linked not only to reduced growth of neighboring plants but also to reduced pollinator visitation and lower sexual reproductive success in native species (Masters and Emery 2015).
However, research on allelopathy in V. amygdalina remains limited and has largely focused on its use as a biopesticide (Mkindi et al. 2017; Tembo et al. 2018). However, phytochemical screening of ethanol extracts has identified alkaloids, phenols, flavonoids, terpenoids, saponins, tannins, and cardiac glycosides (Tura et al. 2024), suggesting considerable allelopathic potential that could contribute to invasion success.
To provide empirical evidence, we compared leaf materials from V. amygdalina with those from the invasive vine Mikania micrantha by applying leaf‐homogenate extracts to seeds of three common crops (rice, water spinach ( Ipomoea aquatica Forssk.), and Chinese cabbage ( Brassica rapa var. chinensis)), using distilled water as a control. By monitoring germination over time, we evaluated whether V. amygdalina inhibits germination and early establishment. Leaf extracts of V. amygdalina significantly reduced germination vigor of rice and water spinach and markedly inhibited radicle and plumule growth. Overall, the inhibitory effects of V. amygdalina on germination and early seedling establishment were stronger than those of M. micrantha (Figure 2). M. micrantha is widely reported to possess strong allelopathic potential: leaf and/or root extracts and isolated allelochemicals can inhibit germination and seedling growth of multiple recipient species (Wu et al. 2009, 2015; Ma et al. 2020). Together, these findings support the view that V. amygdalina may also exhibit pronounced allelopathic effects.
FIGURE 2.

Allelopathic effects of leaf extracts from Vernonia amygdalina and the invasive Mikania micrantha on seed germination of three crop species. Seeds of rice ( Oryza sativa ), water spinach ( Ipomoea aquatica ), and Chinese cabbage ( Brassica rapa var. chinensis) were treated with distilled water (control) or leaf extracts (0.05 g L−1) prepared from M. micrantha or V. amygdalina. (A) Representative photographs taken 3 days after incubation show delayed germination and reduced radicle and plumule growth under the V. amygdalina treatment compared with the control and M. micrantha treatments. (B) Mean germination rate (±SD) calculated from measurements on days 1, 4, and 7 during a 7‐day observation period. For each crop species and treatment, 60 seeds were used (three replicates). Different letters above bars indicate significant differences among treatments within the same crop species (Duncan's multiple range test, p < 0.05; n = 9).
6. Plant Defense Mechanisms
In addition to allelopathy, another important mechanism is defense against herbivores. Invasive plants often exhibit effective defense mechanisms. Compared to native species, invasive plants may be attacked less frequently by herbivorous pests. Early work proposed the “enemy release hypothesis,” which suggests that invaders face fewer specialized enemies in introduced habitats (Blossey and Notzold 1995). More recent studies indicate that invasive plants still experience pressure from generalist herbivores (Sun et al. 2023), which may select for enhanced defenses (Zhai et al. 2024).
V. amygdalina, commonly called bitter leaf, has a characteristic bitter taste caused by anti‐nutritional compounds such as alkaloids, saponins, tannins, and glycosides (Bonsi et al. 1995; Farombi and Owoeye 2011). In Africa, V. amygdalina has been investigated as an alternative insecticide for pest control (Green et al. 2017; Mkindi et al. 2017), indicating strong pest‐defense capacity. In newly introduced areas, reduced herbivore pressure—combined with intrinsic defense traits—could facilitate population growth and spread.
7. Climatic Distribution
Vernonia amygdalina occurs naturally across tropical Africa, from East Guinea to Somalia and northeastern South Africa, and it is also reported from Yemen. It is widely cultivated as a vegetable in Benin, Nigeria, Cameroon, Gabon, and the Democratic Republic of Congo, with smaller‐scale cultivation in neighboring regions (Houegban et al. 2024). GBIF (Global Biodiversity Information Facility) occurrence records show a strong concentration of records in tropical Africa, consistent with its native range. Records outside Africa are generally sparse and scattered, with comparatively more occurrences in Brazil. In China, GBIF currently documents the species only from Taiwan (Figure 3). The species typically occurs along riverbanks, lake shores, forest margins, woodlands, and grasslands, in areas with mean annual rainfall of 750–2000 mm and elevations up to 2800 m (Farombi and Owoeye 2011; Houegban et al. 2024). Although drought tolerant, V. amygdalina performs best in humid, humus‐rich soils (Kaur et al. 2019; Houegban et al. 2024; Khatri et al. 2025a).
FIGURE 3.

Global distribution of Vernonia amygdalina based on GBIF (Global Biodiversity Information Facility) occurrence records. Yellow points represent georeferenced occurrences compiled in the GBIF database, showing a strong concentration in tropical Africa and generally sporadic records elsewhere, including a single recorded region in China (Taiwan) and comparatively more records in Brazil.
China spans climates from tropical to cold temperate. South of the Yangtze River, the subtropical monsoon zone is characterized by alternating influences of tropical maritime and polar continental air masses. This region has abundant heat resources, with mean annual temperatures of 13°C–20°C and accumulated temperatures above 10°C of 4000°C–6500°C (Sun et al. 2008). In January, mean temperatures south of the Yangtze River generally exceed 0°C (2°C–10°C) and reach 10°C–12°C in southern subtropical areas of Guangdong and Guangxi. Annual precipitation typically ranges from 800 to 1600 mm (Yao et al. 2008). Such climatic similarity to the species' native tropical range may facilitate survival and reproduction in southern China. This similarity may reduce environmental resistance and increase the likelihood of establishment and spread.
8. Introduction and Cultivation Practices
Vernonia amygdalina has notable medicinal value. Its bitter leaves are described as “cool” in traditional use and are used for detoxification and treatment of several ailments. In China, it is commonly used as a folk remedy for fever and gastrointestinal disorders. Fresh leaves may be eaten raw, decocted, dried and ground into powder, or applied externally (Liu et al. 2022). In addition, leaf extracts have been investigated for roles in targeted cancer therapies (Johnson et al. 2017; Yao et al. 2020; Liu et al. 2022).
In southern China, these perceived benefits have promoted widespread cultivation (Yao et al. 2020; Liu et al. 2022). However, poor management during cultivation and human‐mediated escape into the wild may increase invasion risk. Surrounding habitats near cultivation sites may function as “stepping stones” that facilitate spread. Seeds or vegetative propagules can disperse through natural pathways, expanding the species' range and elevating invasion potential.
To integrate the diverse lines of evidence in this study and present the logical chain more intuitively, we constructed a conceptual framework (Figure 4) depicting the potential invasion threat posed by V. amygdalina in China. The framework begins with propagule pressure associated with introduction and cultivation, and it integrates climatically suitable regions in China with reproductive, growth, allelopathic, and other life‐history traits, thereby indicating invasion potential and providing a basis for subsequent monitoring, early warning, and management (Figure 4).
FIGURE 4.

Conceptual framework illustrating the potential invasion of Vernonia amygdalina in China. This framework starts from the propagule potential associated with its introduction and cultivation and integrates climatically suitable regions in China with its reproductive, growth, allelopathic, and other traits to indicate its invasion potential in China.
9. Conclusions
Although currently recorded only sporadically in southern China (Peng et al. 2018; Yao et al. 2020; Yang et al. 2023), V. amygdalina shows a non‐negligible invasion risk of establishment and spread. In particular, high reproductive capacity (seed production plus vegetative regeneration), potential allelopathic effects, and strong defense traits may facilitate establishment and competitive dominance once the species escapes cultivation. Climatic similarity between southern China and the native tropical range, together with ongoing introduction and cultivation, could further increase propagule pressure and create “stepping‐stone” sites for spread. We therefore recommend precautionary management, including targeted monitoring around cultivation areas, early detection and rapid response to escaped individuals, and clearer guidance on planting and disposal practices, to prevent this species from transitioning from an occasional alien to an established invader.
Author Contributions
Lei Gao: conceptualization (equal), funding acquisition (equal), investigation (equal), writing – original draft (equal), writing – review and editing (equal). Jia lin Deng: methodology (equal), software (equal). Shu Ning Liu: data curation (equal), writing – original draft (equal). Yun Lu Ma: data curation (equal), writing – original draft (equal).
Funding
This study was supported by the National Natural Science Foundation of China (Grant No. 31470451) and the Basic and Applied Basic Research Foundation of Guangdong Province (Grant No. 2024A1515011114).
Conflicts of Interest
The authors declare no conflicts of interest.
Acknowledgments
We thank the reviewers for their exhaustive and comprehensive comments on our manuscript.
Data Availability Statement
No additional datasets were generated or analyzed during the current study. All relevant data are included in this article.
References
- Al Harun, M. A. Y. , Robinson R. W., Johnson J., and Uddin M. N.. 2014. “Allelopathic Potential of Chrysanthemoides monilifera Subsp. Monilifera (Boneseed): A Novel Weapon in the Invasion Processes.” South African Journal of Botany 93: 157–166. [Google Scholar]
- Alebie, G. , Urga B., and Worku A.. 2017. “Systematic Review on Traditional Medicinal Plants Used for the Treatment of Malaria in Ethiopia: Trends and Perspectives.” Malaria Journal 16: 307. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Antunes, P. M. , and Schamp B.. 2017. “Constructing Standard Invasion Curves From Herbarium Data‐Toward Increased Predictability of Plant Invasions.” Invasive Plant Science and Management 10: 293–303. [Google Scholar]
- Bieberich, J. , Lauerer M., Drachsler M., Heinrichs J., Müller S., and Feldhaar H.. 2018. “Species‐ and Developmental Stage‐Specific Effects of Allelopathy and Competition of Invasive Impatiens glandulifera on Co‐Occurring Plants.” PLoS One 13: e020584. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Blossey, B. , and Notzold R.. 1995. “Evolution of Increased Competitive Ability in Invasive Nonindigenous Plants ‐ a Hypothesis.” Journal of Ecology 83: 887–889. [Google Scholar]
- Bonsi, M. L. K. , Osuji P. O., Tuah A. K., and Umanna N. N.. 1995. “ Vernonia‐amygdalina as a Supplement to Teff Straw ( Eragrostis tef ) Fed to Ethiopian Menz Sheep.” Agroforestry Systems 31: 229–241. [Google Scholar]
- Buchanan, A. L. 2015. “Effects of Damage and Pollination on Sexual and Asexual Reproduction in a Flowering Clonal Plant.” Plant Ecology 216: 273–282. [Google Scholar]
- Davis, M. A. , Grime J. P., and Thompson K.. 2000. “Fluctuating Resources in Plant Communities: A General Theory of Invasibility.” Journal of Ecology 88: 528–534. [Google Scholar]
- Devenish, A. J. M. , Newton R. J., Midgley J. J., Colville L., Bridle J., and Sumner S.. 2024. “Mutualistic Interactions Facilitate Invasive Species Spread.” Functional Ecology 39: 254–267. [Google Scholar]
- Fan, J. A. , and Zhao X. Q.. 1997. “Research on Risk Assessment System and Method for Alien Pests of Crops.” Plant Quarantine 12: 14–18. [Google Scholar]
- Farombi, E. O. , and Owoeye O.. 2011. “Antioxidative and Chemopreventive Properties of Vernonia amygdalina and Garcinia kola .” International Journal of Environmental Research and Public Health 8: 2533–2555. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Fartyal, A. , Bhambra G. K., Joshi V., Joshi C., Bargali K., and Bargali S. S.. 2025. “Assessing the Potential of Three Invasive Alien Plants as Possible Feedstock for the Production of Biochar and Crop Productivity.” Journal of Soil Science and Plant Nutrition 25: 5916–5932. [Google Scholar]
- Gao, L. , Hou B., Cai M. L., Zhai J. J., Li W. H., and Peng C. L.. 2018. “General Laws of Biological Invasion Based on the Sampling of Invasive Plants in China and the United States.” Global Ecology and Conservation 16: e00448. [Google Scholar]
- Green, P. W. C. , Belmain S. R., Ndakidemi P. A., Farrell L. W., and Stevenson P. C.. 2017. “Insecticidal Activity of Tithonia diversifolia and Vernonia amygdalina .” Industrial Crops and Products 110: 15–21. [Google Scholar]
- Hao, J. H. , Qiang S., Chrobock T., van Kleunen M., and Liu Q. Q.. 2011. “A Test of Baker's Law: Breeding Systems of Invasive Species of Asteraceae in China.” Biological Invasions 13: 571–580. [Google Scholar]
- Heimovitz, P. J. , Kocovsky P. M., and English J. J.. 2024. Invasive Species Reserch—Science for Prevention, Detection, Containment, and Control. U.S. Geological Survey. [Google Scholar]
- Herrera, I. , and Nassar J. M.. 2009. “Reproductive and Recruitment Traits as Indicators of the Invasive Potential of Kalanchoe daigremontiana (Crassulaceae) and Stapelia gigantea (Apocynaceae) in a Neotropical Arid Zone.” Journal of Arid Environments 73: 978–986. [Google Scholar]
- Holdrege, M. C. , Palmquist K. A., Schlaepfer D. R., et al. 2024. “Climate Change Amplifies Ongoing Declines in Sagebrush Ecological Integrity.” Rangeland Ecology & Management 97: 25–40. [Google Scholar]
- Houegban, J. , Aglinglo L. A., N'Danikou S., et al. 2024. “Traditional African Vegetables' Seed Access and Management Practices: Case of Vernonia amygdalina (Delile) in Southern Benin.” Frontiers in Sustainable Food Systems 8: 1276736. [Google Scholar]
- Ijeh, I. I. , and Ejike C. E. C. C.. 2011. “Current Perspectives on the Medicinal Potentials of Vernonia amygdalina Del.” Journal of Medicinal Plant Research 5: 1051–1061. [Google Scholar]
- Johnson, W. , Tchounwou P. B., and Yedjou C. G.. 2017. “Therapeutic Mechanisms of Vernonia amygdalina Delile in the Treatment of Prostate Cancer.” Molecules 22: 1594. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Joshi, C. , Joshi V., Fartyal A., Bargali B., and Bargali S. S.. 2025. “Altered Composition and Structure of Plant Communities in Response to Lantana camara Invasion in Forest Ecosystems of Kumaun Himalaya, India.” Trees, Forests and People 21: 100947. [Google Scholar]
- Kato‐Noguchi, H. , and Kurniadie D.. 2022. “Allelopathy and Allelochemicals of Leucaena leucocephala as an Invasive Plant Species.” Plants‐Basel 11: 1672. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Kaur, D. , Kaur N., and Chopra A.. 2019. “A Comprehensive Review on Phytochemistry and Pharmacological Activities of Vernonia amygdalina .” Journal of Pharmacognosy and Phytochemistry 8: 2629–2636. [Google Scholar]
- Khatri, K. , Bargali K., and Bargali S. S.. 2025a. “Invasion Consequences: Suppression of Native Tree Seedlings by Ageratina adenophora and the Potential of Its Composted Leaves as an Organic Amendment.” Plant Ecology 226: 1081–1094. [Google Scholar]
- Khatri, K. , Bargali K., and Bargali S. S.. 2025b. “Mitigating the Toxic Effects of Ageratina adenophora Rhizospheric Soil on Wheat Crop Through Biochar‐Based Soil Amendments.” Journal of Soil Science and Plant Nutrition 25: 5439–5454. [Google Scholar]
- Khatri, K. , Negi B., Bargali K., and Bargali S. S.. 2022. “Effects of Elevation and Habitat on Leaf and Reproductive Traits of Ageratina adenophora (Sprengel) King & Robinson.” South African Journal of Botany 147: 859–870. [Google Scholar]
- Khatri, K. , Negi B., Bargali K., and Bargali S. S.. 2023. “Phenotypic Variation in Morphology and Associated Functional Traits in Ageratina adenophora Along an Altitudinal Gradient in Kumaun Himalaya, India.” Biologia 78: 1333–1347. [Google Scholar]
- Kim, Y. O. , and Lee E. J.. 2011. “Comparison of Phenolic Compounds and the Effects of Invasive and Native Species in East Asia: Support for the Novel Weapons Hypothesis.” Ecological Research 26: 87–94. [Google Scholar]
- Li, B. , and Chen J. K.. 2002. “Ecology of Biological Invasions: Achievements and Chanllenges.” World Scientific Series in R&D Management 24: 11. [Google Scholar]
- Li, B. , Xu B. S., and Chen J. K.. 2001. “Perspective on General Trends of Plant Invasion With Special Reference to Alien Weed Flora of Shanghai.” Biodiversity Science 9: 446–457. [Google Scholar]
- Li, H. R. , Yan J., Du C., and Yan X. L.. 2022. “Current Status and Suggestions of Research on Invasive Risk Assessment of Alien Plants in China.” Acta Ecologica Sinica 42: 6451–6463. [Google Scholar]
- Li, Z. Y. , and Xie Y.. 2002. Alien Invasive Species in China. China Forestry Publishing House. [Google Scholar]
- Liu, X. Z. , Yang R. J., Xu Q. N., et al. 2022. “Tautomeric Phytosterols From Vernonia amygdalina Delile and Their Anti‐Cervical Cancer Activity.” Bioorganic Chemistry 128: 106068. [DOI] [PubMed] [Google Scholar]
- Ma, H. Y. , Chen Y., Chen J. H., Zhang Y. Q., Zhang T., and He H.. 2020. “Comparison of Allelopathic Effects of Two Typical Invasive Plants: Mikania micrantha and Ipomoea cairica in Hainan Island.” Scientific Reports 10: 11332. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Mariani, C. , Cabrini R., Danin A., et al. 2010. “Origin, Diffusion and Reproduction of the Giant Reed ( Arundo donax L.): A Promising Weedy Energy Crop.” Annals of Applied Biology 157: 191–202. [Google Scholar]
- Martín‐Forés, I. , Acosta‐Gallo B., Castro I., de Miguel J. M., del Pozo A., and Casado M. A.. 2018. “The Invasiveness of Hypochaeris glabra (Asteraceae): Responses in Morphological and Reproductive Traits for Exotic Populations.” PLoS One 13: e0198849. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Masters, J. A. , and Emery S. M.. 2015. “The Showy Invasive Plant Ranunculus ficaria Facilitates Pollinator Activity, Pollen Deposition, but Not Always Seed Production for Two Native Spring Ephemeral Plants.” Biological Invasions 17: 2329–2337. [Google Scholar]
- Mkindi, A. , Mpumi N., Tembo Y., et al. 2017. “Invasive Weeds With Pesticidal Properties as Potential New Crops.” Industrial Crops and Products 110: 113–122. [Google Scholar]
- Negi, B. , Khatri K., Bargali S. S., and Bargali K.. 2023. “Invasive Ageration adenophora (Asteraceae) in Agroecosystems of Kumaun Himalaya, India: A Threat to Plant Diversity and Sustainable Crop Yield.” Sustainability‐Basel 15: 10748. [Google Scholar]
- Negi, B. , Khatri K., Bargali S. S., Bargali K., and Fartyal A.. 2025. “Phenological Behaviour of Ageratina adenophora Compared With Native Herb Species Across Varied Habitats in the Kumaun Himalaya.” Plant Ecology 226: 237–249. [Google Scholar]
- Peng, X. C. , Pan Y., Zhu X. Y., Zhou X. M., Gao J., and Wang C. Y.. 2018. “Morphological Characters and Wind Dispersal Property of Pappose Seeds for Seven Common Compositae Weeds in Yunnan, China.” Journal of Yunnan University 40: 1024–1033. [Google Scholar]
- Pfadenhauer, W. G. , and Bradley B. A.. 2024. “Quantifying Vulnerability to Plant Invasion Across Global Ecosystems.” Ecological Applications 34: e3031. [DOI] [PubMed] [Google Scholar]
- Pili, A. N. , Leroy B., Measey J. G., et al. 2024. “Forecasting Potential Invaders to Prevent Future Biological Invasions Worldwide.” Global Change Biology 30: e17399. [DOI] [PubMed] [Google Scholar]
- Qi, S. S. , Liu Y. J., Dai Z. C., et al. 2020. “Allelopathy Confers an Invasive Wedelia trilobata Higher Resistance to Generalist Herbivore and Pathogen Enemies Over Its Native Congener.” Oecologia 192: 415–423. [DOI] [PubMed] [Google Scholar]
- Reaser, J. K. , Burgiel S. W., Kirkey J., Brantley K. A., Veatch S. D., and Burgos‐Rodriguez J.. 2020. “The Early Detection of and Rapid Response (EDRR) to Invasive Species: A Conceptual Framework and Federal Capacities Assessment.” Biological Invasions 22: 1–19. [Google Scholar]
- Rodrigues, T. , Kratina P., Setubal R. B., et al. 2024. “Interaction Between Climate Change Scenarios and Biological Invasion Reveals Complex Cascading Effects in Freshwater Ecosystems.” Global Change Biology 30: e17540. [DOI] [PubMed] [Google Scholar]
- Seebens, H. , Blackburn T. M., Dyer E. E., et al. 2017. “No Saturation in the Accumulation of Alien Species Worldwide.” Nature Communications 8: 14435. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Semizer‐Cuming, D. , Finkeldey R., Nielsen L. R., and Kjær E. D.. 2019. “Negative Correlation Between Ash Dieback Susceptibility and Reproductive Success: Good News for European Ash Forests.” Annals of Forest Science 76: 219. [Google Scholar]
- Shea, K. , and Chesson P.. 2002. “Community Ecology Theory as a Framework for Biological Invasions.” Trends in Ecology & Evolution 17: 170–176. [Google Scholar]
- Sun, X. , Sun Y. M., Cao X. Y., et al. 2023. “Trade‐Offs in Non‐Native Plant Herbivore Defences Enhance Performance.” Ecology Letters 26: 1584–1596. [DOI] [PubMed] [Google Scholar]
- Sun, Y. L. , Yan X. D., and Xie D. T.. 2008. “A New Method of Vegetation‐Climate Classification in China.” International Journal of Climatology 28: 1163–1173. [Google Scholar]
- Svensson, J. R. , Nylund G. M., Cervin G., Toth G. B., and Pavia H.. 2013. “Novel Chemical Weapon of an Exotic Macroalga Inhibits Recruitment of Native Competitors in the Invaded Range.” Journal of Ecology 101: 140–148. [Google Scholar]
- Teller, B. J. , Zhang R., and Shea K.. 2016. “Seed Release in a Changing Climate: Initiation of Movement Increases Spread of an Invasive Species Under Simulated Climate Warming.” Diversity and Distributions 22: 708–716. [Google Scholar]
- Tembo, Y. , Mkindi A. G., Mkenda P. A., et al. 2018. “Pesticidal Plant Extracts Improve Yield and Reduce Insect Pests on Legume Crops Without Harming Beneficial Arthropods. Front.” Plant Science 9: 1425. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Tura, A. M. , Anbessa M., Tulu E. D., and Tilinti B. Z.. 2024. “Exploring Vernonia amygdalina Leaf Extracts for Phytochemical Screening and Its Anti‐Bacterial Activities.” International Journal of Food Properties 27: 960–974. [Google Scholar]
- Turbelin, A. J. , Hudgins E. J., Catford J. A., et al. 2024. “Biological Invasions as Burdens to Primary Economic Sectors.” Global Environmental Change 87: 102858. [Google Scholar]
- Wan, J. Z. , Wang C. J., Tan J. F., and Yu F. H.. 2017. “Climatic Niche Divergence and Habitat Suitability of Eight Alien Invasive Weeds in China Under Climate Change.” Ecology and Evolution 7: 1541–1552. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Wang, K. L. , Dou P. P., Miao Z. Z., et al. 2024. “Seed Germination and Seedling Growth Response of Leymus chinensis to the Allelopathic Influence of Grassland Plants.” Oecologia 204: 899–913. [DOI] [PubMed] [Google Scholar]
- Weber, E. , and Li B.. 2008. “Plant Invasions in China: What Is to Be Expected in the Wake of Economic Development?” Bioscience 58: 437–444. [Google Scholar]
- Wu, A. P. , Li Z. L., He F. F., Wang Y. H., and Dong M.. 2015. “Screening Allelochemical‐Resistant Species of the Alien Invasive Mikania micrantha for Restoration in South China.” PLoS One 10: e0132967. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Wu, A. P. , Yu H., Gao S. Q., et al. 2009. “Differential Belowground Allelopathic Effects of Leaf and Root of Mikania micrantha .” Trees‐Structure and Function 23: 11–17. [Google Scholar]
- Yang, W. J. , Sun S. X., Wang N. X., et al. 2023. “Dynamics of the Distribution of Invasive Alien Plants (Asteraceae) in China Under Climate Change.” Science of the Total Environment 903: 166260. [DOI] [PubMed] [Google Scholar]
- Yao, C. , Yang S., Qian W. H., Lin Z. M., and Wen M.. 2008. “Regional Summer Precipitation Events in Asia and Their Changes in the Past Decades.” Journal of Geophysical Research: Atmospheres 113: 9603. [Google Scholar]
- Yao, S. Z. , Zhao L., Zhonf Y. H., et al. 2020. “Screening of Anti‐Breast Cancer Active Fractions of Vernonia amygdalina .” Journal of Guangxi University (Natural Science Edition) 45: 1508–1513. [Google Scholar]
- Zhai, J. J. , Hou B., Hu F. Y., et al. 2024. “Active Defense Strategies for Invasive Plants May Alter the Distribution Pattern of Pests in the Invaded Area.” Frontiers in Plant Science 15: 1428752. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Zheng, H. S. , Mao X. J., Lin Y., Fu K. Y., Qi Z. Y., and Wu Y. B.. 2024. “Reconstructing the Biological Invasion of Noxious Invasive Weed Parthenium hysterophorus and Invasion Risk Assessment in China.” Frontiers in Plant Science 15: 1430576. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Zheng, Y. L. , Feng Y. L., Zhang L. K., et al. 2015. “Integrating Novel Chemical Weapons and Evolutionarily Increased Competitive Ability in Success of a Tropical Invader Chromolaena odorata .” New Phytologist 205: 1350–1359. [DOI] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
No additional datasets were generated or analyzed during the current study. All relevant data are included in this article.
