[go: up one dir, main page]
More Web Proxy on the site http://driver.im/
Next Article in Journal
Thiamine and Thiamine Pyrophosphate as Non-Competitive Inhibitors of Acetylcholinesterase—Experimental and Theoretical Investigations
Previous Article in Journal
Screening of Solvent Systems for Countercurrent Chromatography Separation of Polar Constituents from Ginkgo biloba L. Seeds
You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Compounds Involved in the Invasive Characteristics of Lantana camara

Department of Applied Biological Science, Faculty of Agriculture, Kagawa University, Miki 761-0795, Kagawa, Japan
*
Author to whom correspondence should be addressed.
Molecules 2025, 30(2), 411; https://doi.org/10.3390/molecules30020411
Submission received: 23 December 2024 / Revised: 11 January 2025 / Accepted: 13 January 2025 / Published: 19 January 2025

Abstract

:
Lantana camara L. is native to tropical America and has naturalized in many other tropical, subtropical, and temperate regions in Asia, Africa, Oceania, North and South America, and Europe. L. camara infests diverse habitats with a wide range of climatic factors, and its population increases aggressively as one of the world’s 100 worst invasive alien species. Its infestation reduces species diversity and abundance in the natural ecosystems and reduces agricultural production. The life history characteristics of L. camara, such as its high reproductive ability and high adaptive ability to various environmental conditions, may contribute to its ability to infest and increase its population. Possible evidence of the compounds involved in the defense functions of L. camara against natural enemies, such as herbivore mammals and insects, parasitic nematodes, pathogenic fungi and bacteria, and the allelochemicals involved in its allelopathy against neighboring competitive plant species, have accumulated in the literature over three decades. Lantadenes A and B, oleanonic acid, and icterogenin are highly toxic to herbivore mammals, and β-humulene, isoledene, α-copaene thymol, and hexadecanoic acid have high insecticidal activity. β-Caryophyllene and cis-3-hexen-1-ol may function as herbivore-induced plant volatiles which are involved in sending warning signals to undamaged tissues and the next plants of the same species. Farnesol and farnesal may interrupt insect juvenile hormone biosynthesis and cause abnormal metamorphosis of insects. Several triterpenes, such as lantanolic acid, lantoic acid, pomolic acid, camarin, lantacin, camarinin, ursolic acid, and oleanonic acid, have demonstrated nematocidal activity. Lantadene A, β-caryophyllene, germacrene-D, β-curcumene, eicosapentaenoic acid, and loliolide may possess antimicrobial activity. Allelochemicals, such as caffeic acid, ferulic acid, salicylic acid, α-resorcylic acid, p-hydroxybenzoic acid, vanillic acid, unbelliferone, and quercetin, including lantadenes A and B and β-caryophyllene, suppress the germination and growth of neighboring plant species. These compounds may be involved in the defense functions and allelopathy and may contribute to L. camara’s ability to infest and to expand its population as an invasive plant species in new habitats. This is the first review to focus on how compounds enhance the invasive characteristics of L. camara.

Graphical Abstract">
Graphical Abstract

1. Introduction

Lantana camara L., belonging to the Verbenaceae family, is a perennial shrub, 1–4 m in height, with quadrangular or cylindrical stems and small prickles. Multiple stems frequently arise at the base of the main stems and form dense impenetrable stands. The oval leaves are opposite and serrate [1,2,3,4] (Figure 1). The native range of the species is tropical America, and it was introduced into many counties as an ornamental plant [5,6,7]. L. camara has spread across tropical, subtropical, and temperate regions in Asia, Africa, Oceania, North and South America, and Europe [1,2,3,8].
L. camara infestations were monitored in 134 plots from 1997 to 2008 in the Biligiri Rangaswamy Temple Wildlife sanctuary (540 km2) in the Western Ghats of India. L. camara occupied 41% and 81% of the plots in 1997 and 2008, respectively, and the mean density of L. camara stands increased 4-fold from 1997 to 2008 [9]. The total area of infestation of L. camara in India has already covered 13 million ha [10]. In South Africa, the species occupied 25,000–30,000 ha in 1962 and 2.2 million ha in the early 1980s [7,11]. The species occupied more than 5 million ha of coastal and sub-coastal Queensland and NSW in Australia. Its distribution has been expanding from the Torres Strait throughout eastern Queensland to the southern border of NSW and Western Australia, the Northern Territory, and Victoria [12]. Considering the risk of its invasiveness, L. camara has been listed in the world’s 100 worst invasive alien species by IUCN [13].
A global spatial invasion risk assessment of L. camara using a random forest modeling approach showed that L. camara has already infested and/or established itself in 114 countries. The areas with a high invasion risk were estimated to be between 35° N and 35° S latitude, and an additional 27 countries are at risk of serious invasion [14]. The global climate change warming trend increases the risk of invasion of L. camara in all continents except Antarctica [14,15,16]. The risk of invasion of Europe will increase by 251%, compared to current levels, from 2061 to 2080, and 28 countries will face a risk increase of over 50% [14].
L. camara causes significant impacts on natural ecosystems and agricultural production [5,11]. Infestation of L. camara interrupts the regeneration process of native plant species and lowers species richness and density in native plant communities, including in endangered plant species. It was observed that juvenile plant densities of native plant species were lower in areas infested with L. camara than in non-infested areas [9,17,18,19,20]. L. camara was reported to occupy 23% of the total area of protected areas (1633 ha of 7006 ha) of the Lehri Nature Park in Pakistan [21], and it has already infested many other protected areas [9,22,23,24]. The species has adversely affected 1300 native species, including endangered plant species in Australia and Hawaii [2,25].
The infestation of L. camara also affects soil properties, increasing total carbon and phosphate concentrations and soil moisture [26,27]. The modification of the soil properties affects species composition and ecosystem structure and functions, resulting in alteration of food webs and the habitats of vertebrate and invertebrates [28]. L. camara infestation lowers the abundance and richness of invertebrates, birds, and mammals [29,30,31,32,33]. In addition, L. camara is easy to burn, and increases fire risk in dry rainforests by shifting the distribution of available fuel beds and providing a more continuous fuel layer [34].
L. camara infestation causes a major problem in most agricultural areas. Its large, impenetrable thickets reduce grass abundance and species in pastures and block the movement of domestic stocks to waterholes [8]. L. camara has the negative effects on the farm operation and production. The infestation caused the reduction in maize and cassava (main crops in the area) yield by 26–50%, forage availability by over 50%, and medicinal plant availability in eastern Africa [35]. The species causes significant reductions in coconut plantations in the Philippines, Fiji, Solomon Islands, and Vanuatu [36,37], oil palm and rubber plantations in Malaysia, banana plantations in Australia and Samoa [8], citrus plantations in Florida [38], tea plantations in India and Indonesia [39], and timber plantations in Australia, South Africa, India, and Indonesia [39,40,41]. The considerable resources are spent on L. camara management. The control annual cost was estimated to be ca. INR 9000 per hectare (reported in 2009) in India [42], R 1.7 million (reported in 1999) in South Africa, and AUD 104 million (reported in 2007) in Australia only for stock-farming industry [7,8].
L. camara shows high genetic variations and high levels of adaptive ability to various environmental conditions [6,43,44]. L. camara infests into diverse habitats with a wide range of climatic factors. L. camara generally grows well in open habitats, such as sparse forests, forest margins, grasslands, riparian zones, and coastal plains. It also infests into the disturbed areas, such as forestry plantations, orchards, agriculture fields, abandoned land, roadsides, and railroads [5,11,19,20]. L. camara grows in tropical, subtropical, and temperate climates, with mean annual precipitation ranging from 4000 mm to 1000 mm, at 13 °C for the lower limit of the mean temperature. However, the species tolerates the annual precipitation as low as 200 mm and at 0 °C for the absolute minimum temperature [2,5]. L. camara can grow on a variety of soil types, pH values between 4.5 and 8.5, nutrient-rich to nutrient-poor soil, moist to dry soil, or sandy soil to clay soil [6,28].
L. camara grows and flowers throughout the year under good growing conditions [5,6,10] and produces 12,000 fruits, containing seeds, per plant in each year [28,45]. The seeds are mainly dispersed by birds and water flow, including flooding water [5,6]. The seed viability was reported to be ranging from 2 to 5 years, and the germination rate was 20–50% under both laboratory and field conditions [6,28]. However, the germination rate increased after the birds feeding because of the digestion of seed pulp [6,8]. L. camara also reproduces asexually. The regeneration occurs through the ramet sprouting. The ramets arise from the dormant buds at the bases of the stems [28]. These observations suggest that L. camara has the high reproductive adaptivity and high adaptive ability to various environmental conditions [6,28]. Such characteristics of the life history may contribute to the infestation and expanding population of L. camara in the introduced ranges (Figure 2).
Several review articles have summarized the biology, impacts, and management of L. camara [5,6,7,8,9,10,11,28,30,46]. Other review articles have summarized the biologically active compounds of L. camara for the purpose of the development of medicines and pesticides [47,48,49,50,51,52,53,54]. However, there has been no review article focusing on the compounds involved in the invasive characteristics of L. camara. This is the first review article providing an overview of the compounds involved in the invasive characteristics of L. camara and the action mechanisms of these compounds. The literature was searched using a combination of the predominant online search engines: Scopus, ScienceDirect, and Google Scholar and all possible combinations of L. camara with the following words: invasiveness, adaptively, ecology, habitat, reproduction, impact, natural enemy, herbivore, nematode, insecticidal activity, fungicidal activity, symbiosis, pharmacology, allelopathy, allelochemical, and secondary metabolite.

2. Defense Compounds Against Herbivore Mammals

The ingestion of L. camara plants causes critical symptoms of photosensitivity, hepatomegaly, jaundice, and nephrosis in herbivore mammals, including livestock such as cattle, sheep, goats, rabbits, buffaloes and horses [48,55]. The incidents of L. camara poisoning occur when adequate fodder supply is limited during drought and flooding conditions and when animals are transported from Lantana-free areas to Lantana-infested areas [56,57,58]. After feeding on the leaves, stems, and/or roots of L. camara, these animals suffer from constipation in 2 h, stasis in 4–6 h, photosensitization in 24–48 h, and then swelling of their muzzles and eyelids. Toxic substances, such as lantadene A, lantadene B, lantadene C, lantadene D, oleanonic acid, and icterogenin in L. camara plants, are absorbed through the gastrointestinal tracts of these animals and transported to the liver in portal blood. Then, these toxic substances cause cholestasis and hepatotoxicity, and induce hepatic necrosis [59]. These compounds also cause jaundice and nephrosis. It was observed that 74 of 170 heifers were dead in a few weeks after the feeding of L. camara [59], and 40% of mice were dead [60]. The severity of the symptoms depends on the quantity of foliage taken [57,58]. The LD50 value of the partially purified lantadene powder gave to sheep by intravenous injection was 1–3 mg/kg body weight, while the LD50 value of the lantadene powder by oral administration was 60 mg/kg body weight [61]. Lantadene A and lantadene B are the major constituents among these toxic substances in L. camara, and lantadene A is responsible for most of the toxic effects [58,62]. Lantadene A and lantadene B are metabolized into toxic derivatives in vivo, named as reduced lantadene A and reduced lantadene B, respectively [62].
Chemical structures of lantadenes and reduced lantadenes have been determined and are shown in Figure 3 [63,64,65,66]. Lantadenes A, B, C, and D are similar structures, except for the side chain at C1 position. Atoms C32 and C33 on the side chain are connected by a double bond in lantadenes A and B and by a single bond in lantadenes C and D. The different structures of the side chain of lantadenes A, B, C, and D may affect the toxicity [63,64,66].
Lantana toxicity was reported to be caused through the alteration of the microsome and mitochondrial structures in the liver cells. Lantana leaf powder decreased the protein contents, phospholipid-to-protein ratio, and cholesterol-to-protein ratio in the hepatic microsomes, while the ratio of cholesterol to phospholipid did not change [48,67], suggesting the dissociation of endoplasmic reticulum fragments from the microsomes. Lantana leaf powder also decreased protein contents in the hepatic mitochondrial protein. The activities of glutamate dehydrogenase, succinic dehydrogenase, Mg2+-ATPase, and cytochrome oxidase of the mitochondria were increased, while the activity of NADH–ferricyanide reductase remained unchanged [48]. Lantadene A and reduced lantadene A also affect the hepatic mitochondrial membranes, and reduced lantadene A acts as a mitochondrial uncoupler of oxidative phosphorylation, resulting in decreasing ATP levels in the liver cells [68]. Caspase 3 was detected in the hepatocytes in lantadene-poisoned animals via immunostaining [59]. Caspase 3 is an important regulator and indicator of the apoptosis [69,70]. Thus, lantadene toxicity may cause the apoptosis in the hepatocytes, and the apoptosis plays a significant role in the pathogenesis of Lantana poisoning.
L. camara infestation decreased the species abundance and diversity of herbivore mammals in the Groenkloof Nature Reserve in South Africa. The species abundance and diversity of carnivore mammals also decreased as those of the herbivores decreased [32]. The avoidance of L. camara stands by rodents, such as Lemniscomys rosalia, Mastomys coucha, and Saccostomus campestris, was observed in the Groenkloof Nature Reserve [32]. These observations suggest that L. camara produces the toxic substances, protects form the feeding of herbivorous mammals, and affects the species abundance and diversity of the herbivorous and carnivorous mammals.

3. Defense Compounds Against Herbivorous Insects

The feeding activity of herbivorous insects often causes serious damages to the growth, development, and regeneration processes of several plant species [71,72,73]. Therefore, many plant species have developed protective traits against herbivorous insect attacks [74,75,76,77]. It was also reported that many invasive plant species produce certain compounds, which have the defense functions against herbivorous insects [75,78,79].
During the field surveys for the natural enemies of L. camara in its native ranges, the leaf-feeding mirid, Falconia intermedia, was identified as a potential biocontrol agent of L. camara. Falconia intermedia is one of the most abundant and damaging natural enemies of L. camara in the native ranges [80,81]. Therefore, Falconia intermedia was released as a biocontrol agent of L. camara in South Africa in 1999 and Australia in 2000 [82,83]. Larvae and adults of Falconia intermedia feed on the leaves of L. camara and cause severe chlorosis, defoliation, and a reduction in the flowering. The lifetime of the adults is about three weeks, and the females lay 2–3 eggs per day on the undersides of the leaves of L. camara. The development of the larvae is completed in 20–25 days [83,84]. Falconia intermedia initially colonized well in the L. camara stands, and rapidly increased its population size. However, the population of Falconia intermedia disappeared within a few years at almost all sites in South Africa [82]. The attempt of the biological control of L. camara using Falconia intermedia also resulted in very little success in Australia [8].
L. camara induces the physical and chemical defense responses within eight weeks after the insect damage caused by Falconia intermedia [85,86]. L. camara increases its leaf toughness and trichome density on the newly developed leaves [85]. Leaf toughness depends on the deposition of lignin, cellulose, suberin, sclerencyma fibers, xylem, and collenxhymas, and the tough leaves can protect from the attacks of the insect feedings. The trichomes prevented attacks from the insect feeding and oviposition [87,88,89,90].
L. camara also increased 2.5-fold in the emission of β-caryophyllene after the feeding of Falconia intermedia [86]. β-Caryophyllene has been reported to act as the herbivore-induced plant volatiles (HIPVs) in other several plant species, and the emission of β-caryophyllene increased in response to the attacks of herbivorous insects [91,92,93,94,95,96]. cis-3-Hexen-1-ol is one of the major constituents in the essential oil of L. camara [94], and is also known to act as HIPV [95]. The different bouquets of HIPVs (chemical competition and concentration) are emitted by several plant species following the herbivore feeding [95,96].
The emission of HIPVs works for the plants in two ways [95,96,97]. (1) The chemical signals from the damaged plant tissues to the undamaged tissues of the damaged plants and to the adjacent same plant species: Undamaged tissues of the plants and neighboring plants can realize tomorrow’s herbivorous insect attacks and prepare the physical defense responses, such as the increasing leaf toughness and trichome density. (2) HIPVs attract and stimulate the predator insects to hunt the herbivorous insects as their prey. The predator insects receive HIPVs by the olfactory sensilla in their antennae [96]. The action of the predator insects to HIPVs is different from the predator species, and only particular HIPVs can stimulate the hunting behavior of the given predators. The stimulated hunting behavior of the predators reduces number of the herbivorous insects, and further feeding damages [95,96,97]. Therefore, the increasing emission of β-caryophyllene with cis-3-hexen-1-ol may be involved in the indirect defense responses, avoiding the feeding damages by the herbivorous insects.
The ethanol extracts of L. camara leaves increased the mortality of the moth larvae of the cotton leafworm Spodoptera litura [98] and another moth larvae of the cabbage cluster caterpillar Crocidolomia pavonana [99]. The LC50 values of the extracts for Spodoptera litura were 16,347 ppm and 3548 ppm at 24 h and 48 h after the extract application, respectively [98]. The n-hexane extracts of L. camara leaves increased the mortality of the larvae of the red cotton stainer Dysdercus koenigii and also cause its abnormal metamorphosis from the larvae to adult insects. The active compounds were identified as β-caryophyllene and hexadecanoic acid through a GC-MS analysis [100]. Hexadecanoic acid has been reported for its antibacterial activity [101]. Farnesol and farnesal were also identified in the extracts of L. camara leaves [100]. Farnesol and farnesal are the intermediates of the insect juvenile hormone biosynthesis pathway via mevalonic acid. The juvenile hormone is involved in the insect metamorphosis [102,103]. Application of the extracts may disturb the juvenile hormone biosynthesis and cause the abnormal metamorphosis of the larvae [100]. In addition, the n-hexane extracts of L. camara leaves interrupt the mating behavior of the adults of the red cotton strainer and suppress the egg hatching [104].
The essential oil of L. camara showed the insecticidal and insect repellent activity against the adults of the grain weevil Sitophilus granariesm, and the major constituents in the essential oil were β-caryophyllene, β-humulene, and thymol [105]. The n-hexane extracts and the essential oil of L. camara showed the insecticidal activity against the storage grain pests, such as the bean weevil Callosobruchus maculatus, the maize weevil Sitophilus zeamais [106,107], the wheat weevil Sitophilus granarius [108], the beetle Tribolium castaneum, the cigarette beetle Lasioderma serricorne, and the adzuki bean weevil Callosobruchus chinensis [109,110]. β-Caryophyllene (70%), isoledene (12%), and α-copaene (4.1%) were the major constituents in the essential oil [110]. Incorporation of chipped fresh leaves and stems of L. camara into soil prevented the attacks of the Coptotermes formosanus and Reticulitermes flavipes termites [111]. In addition, L. camara infestation decreased the species abundance and diversity of invertebrates, including insects, in the Groenkloof Nature Reserve in South Africa [24] (Figure 4).
One of the essential factors for the success of the invasive plant species infestation in the introduced ranges is its defense ability against the herbivorous insects [71,72,73,74,75]. Specific monophagous herbivores for certain invasive plant species may be few in the introduced ranges because there is no co-evolutional history between the invasive plants and herbivorous insects in the introduced ranges [112]. It is not clear if all of the insects described in this Section feed on L. camara in the introduced ranges. However, the compounds, which have the insecticidal activity, may contribute to the protection from the feeding activity of the herbivorous insects and contribute to the invasive characteristics of L. camara.

4. Defense Compounds Against Parasitic Nematodes

The parasitic nematodes make galls in the host plant roots and deprive photosynthate and other nutrients from their host plants. This parasitism causes a significant growth restraint in the host plant species and the reduction in the plant vigor and defense ability against other pathogen attacks [113,114,115,116]. Root-knot nematodes Meloidogyne spp. are distributed worldwide, and the host range of their parasitism is wide. Therefore, Meloidogyne spp. are considered to be one of the major pathogenic nematodes [117,118].
The aqueous extracts of L. camara leaves increased the mortality of Meloidogyne incognita and significantly suppressed its egg hatching and root-knot development [119,120]. The aqueous extracts and decomposing leaves of L. camara also suppressed the population density of Meloidogyne javanica and its root-knot development [121,122]. The aqueous extracts of L. camara roots mixed into soil resulted in increasing the mortality of Meloidogyne javanica in the soil and in decreasing its egg hatching [123,124]. These observations suggest that L. camara contains certain compounds, which have nematicidal activity.
Seven triterpenes, such as lantanolic acid, lantoic acid, pomolic acid, ursolic acid, camarinin, camarin, and lantacin, were isolated from aerial parts of L. camara as nematocidal active substances. Lantanolic acid, lantoic acid, and pomolic acid showed 100% mortality of Meloidogyne incognita at a 1 mg/mL concentration after 24 h application, while ursolic acid, camarinin, camarin, and lantacin exhibited 100% mortality of Meloidogyne incognita at 1 mg/mL concentration after 48 h application [125,126]. Oleanonic acid was also isolated from aerial parts of L. camara and showed nematocidal activity [127,128]. Therefore, these compounds may be involved in the nematicidal activity of the extracts of L. camara. In addition, L. camara infestation decreased species abundance and diversity of nematodes in the Groenkloof Nature Reserve in South Africa [24] (Figure 5).

5. Defense Compounds Against Pathogenic Fungi and Bacteria

The plant pathogenic fungi are divided into two groups: (1) biotrophic pathogens, which persist in plants and deprive nutrient from plants, and (2) necrotrophic pathogens, which kill the tissue to extract nutrients from plants. Necrotrophic pathogens cause necrosis and even death of the infected plants [129,130,131]. Fusarium is widely distributed in soil, and some of Fusarium spp. cause the Fusarium diseases, such as wilt, blight, rot, canker, and root necrosis on the host plant species in both agricultural and natural ecosystems. Fusarium oxysporum and Fusarium solani are known to be necrotrophic fungus species [132]. The essential oil of L. camara suppressed the growth of Fusarium oxysporum and Fusarium solani [133,134]. The main constituents of the essential oil were germacrene-D (19.55%), β-caryophyllene (17.53%), and β-curcumene (10.22%) [134]. The aqueous and aqueous ethanol extracts of L. camara leaves suppressed the growth of Fusarium oxysporum [135,136]. Aqueous methanol extracts of L. camara leaves also suppressed the Fusarium oxysporum and Fusarium solani. Lantadene A was identified as the active principal of the extracts [137].
The essential oil of L. camara suppressed the growth of other pathogenic fungi, Corynespora cassiicola, Rhizoctonia solani, Agroathelia rolfsii, and Alternaria brassicicola [133,138]. The main constituents of the essential oil were germacrene-D (19.8%) and β-caryophyllene (19.7%) [138]. Corynespora cassiicola has a wide range of host plant species and causes foliar spots, defoliation, and debilitation to the infected plants [139,140,141]. Rhizoctonia solani is facultative with a wide host range and worldwide distribution. It causes various plant diseases, such as root rot, damping off, and wire stems [142]. Agroathelia rolfsii (syn. Sclerotium rolfsii) usually occurs in soil as a saprotroph but can attack living plants. It has an indiscriminate host range and causes blight and root rot [143]. Alternaria brassicicola is a fungal necrotrophic plant pathogen and causes black spot disease on a wide range of plant species [144].
The methanol extracts of L. camara leaves and flowers suppressed the growth of the pathogenic bacterium Xanthomonas axonopodis. The inhibitory activity of extracts between the leaves and flowers were not clearly different [145]. Xanthomonas axonopodis, belonging to the gamma subdivision of Proteobacteria, infects diverse plant hosts and causes canker and necrotic lesions [146]. Through a molecular docking analysis, eicosapentaenoic acid and loliolide were suggested to be active ingredients of the extracts [145]. It was also reported that L. camara alters the soil microbial communities in the infested areas. The altered soil microbial community, including beneficial symbiosis microbes, enhances the growth and stress tolerance of L. camara [147,148]. Some other invasive plant species, such as Imperata cylindrica, Mimosa pigra, Chromolaena odorata, Fallopia japonica, and Ageratum conyzoides, were reported to alter the soil microbial communities, including rhizobium and AMF communities, by releasing certain compounds and to create a better soil microbial community for these invasive plant species but not for the native plant species. The created soil microbial communities enhance the growth and stress tolerance of these invasive plants [149,150,151,152] (Figure 6).
The observations suggest that L. camara produces the compounds, such as lantadene A, germacrene-D, β-caryophyllene, β-curcumene, eicosapentaenoic acid, and loliolide. These compounds protect it from the infection of the pathogenic fungi and bacteria and may contribute to the invasive characteristic of L. camara.

6. Compounds Involved in Allelopathy

Many invasive plants show relatively high allelopathic activity and release allelochemicals into the neighboring environment, including their rhizosphere soil [153,154,155]. Allelochemicals interrupt the germination, growth, and development of the neighboring plant species. Consequently, these invasive plant species acquire stronger competitive ability against the neighboring plant species and obtain a relatively large quantity of resource, such as nutrients, water, and light in their local plant communities [156,157,158]. The ability of the invasive plant species in the resource acquisition is one of the important factors for their infestation success in the introduced ranges [159,160,161,162,163]. Allelochemicals are synthesized, stored in the certain plant parts, and released through volatilization, root exudation, and decomposition of plant parts in the rhizosphere soil [164,165]. Therefore, allelochemicals have been identified in the extracts of the certain plant tissues (leaves, stems, and roots), volatiles, essential oil, root exudation, and rhizosphere soil [166,167,168].
Aqueous leaf extracts of L. camara inhibited the germination of Cucumis sativus, Phaseolus mungo, Raphanus sativus, Vigna unguiculate, Cicer arietinum [169], and Capsicum annuum and Daucus carota [170]. The aqueous leaf extracts also caused the necrosis of the leaves of Eichhornia crassipes [171] and interrupted the regeneration process of the moss Funaria hygrometrica [172]. Methanol extracts of the stem and leaves of L. camara suppressed the germination and growth of Lolium multiflorum [173]. Soaking water of the L. camara leaves, stem, and/or flowers suppressed the germination and growth of Mimosa pudica [174,175]; Pennisetum americanum, Setaria italica, and Lactuca sativa [176]; Triticum aestivum [177,178]; and Cucurbita pepo, Phaseolus vulgaris, and Lycopersicon esculentum [179] and killed Eichhornia crassipes [180,181]. These observations suggest that the extracts of L. camara possess the allelopathic activity, and L. camara contains certain extractable allelochemicals. Some of these allelochemicals may be released from L. camara plants into the neighboring environments by rain and irrigation water.
When the seeds of Triticum aestivum, Zea mays, Glycine max, Lepidium virginicum, and Abutilon theophrasti were sown into the mixture of the chopped shoots of L. camara and sand, the growth of these seedlings was significantly suppressed [182]. The decomposed residues of the roots, leaves, and/or shoots of L. camara also suppressed the growth of Morrenia odorata [183], Urena lobate, Bidens bipinnata, and Bidens pilosa [184]. Rhizosphere soil of L. camara inhibited the growth of Achyranthes aspera and Albizia lebbeck [185] and the germination and growth of Avena sativa, Cicer arietinum, Hordeum vulgare, and Triticum aestivum [186]. These observations suggest that certain allelochemical may be released during the decomposition process of L. camara plants, and the rhizosphere soil may contain the allelochemicals. These allelochemicals may also be released into the rhizosphere soil through the root exudation and/or the leachate from the living plants by rain and irrigation water.
Lantadene A and lantadene B were found in the rhizosphere soil of L. camara as allelochemicals. Lantadene A and lantadene B inhibited the growth of Eichhornia crassipes and Microcystis aeruginosa at concentrations greater than 13.7 mg/L and 10.8 mg/L, respectively [187]. The essential oil obtained from L. camara leaves also suppressed the seedling growth of Portulaca oleracea. The major compounds of the essential oil were α-curcumene, β-caryophyllene, and γ-muurolene [188] (Figure 7).
Caffeic acid, p-coumaric acid, ferulic acid, gentisic acid, salicylic acid, α-resorcylic acid, β-resorcylic acid, p-hydroxybenzoic acid, vanillic acid, vanillin, methyl coumarin, unbelliferone, and quercetin were identified in the aqueous leaf extracts of L. camara as allelochemicals [189]. Although all the compounds inhibited the root and shoot growth of Lolium multiflorum, the inhibitory activity of unbelliferone, methyl coumarin, and salicylic acid was higher than other compounds [189]. A flavonoid, quercetin, was also identified in some other plant species as an allelochemical and suppressed the growth of several pant species and the mitochondrial function [190,191,192]. A flavone glucoside, vitexin, was isolated from the L. camara leaves as an allelochemical [193] (Figure 7).
Benzoic acid and cinnamic acid derivatives, such as caffeic acid, p-coumaric acid, ferulic acid, gentisic acid, salicylic acid, α-resorcylic acid, β-resorcylic acid, p-hydroxybenzoic acid, vanillic acid, and vanillin, were identified in a wide range of plant extracts and plant rhizosphere soil [156,194,195,196]. The involvement of these compounds in plant allelopathy and their mode of actions have been investigated in many other plant species [196,197,198]. These compounds are synthesized from phenylalanine in the shikimic acid pathway and affect the constitution of lipids and proteins of the plasma membranes of the plant cells [199,200]. Consequently, the plasma membranes lose the transmembrane electrochemical potential, and the depolarization of the membranes occurs. The depolarization causes a nonspecific efflux of both anions and cations, including magnesium, nitrate, potassium, and phosphate ions, and changes water balance in the cells. These compounds were also reported to disturb various enzyme activities involved in the phytohormone synthesis, photosynthesis, protein synthesis, and the secondary metabolites and to interrupt the plant cell division and plant growth and development [196,197,198,199,200]. Therefore, those compounds found in L. camara may affect the structure of the plasma membranes, the transmembrane electrochemical potential, and several enzyme activities involved in the essential metabolism in the plant cells.
Aqueous leaf extracts of L. camara increased reactive oxygen species (ROS) and decreased catalase activity in Eichhornia crassipes leaves, causing the occurrence of the necrosis of the leaves [171]. Catalase converts ROS to molecular oxygen and hydrogen peroxide and reduces the oxygen stress conditions [201,202,203]. Thus, the extracts of L. camara cause oxidative stress conditions and interrupt the enzyme activity for the ROS extinction. Anther invasive plant species, Mikania micrantha, was also reported to increase the ROS in the neighboring plant species due to the emission of β-caryophyllene. β-Caryophyllene causes the oxidative stress conditions [204]. β-Caryophyllene was also identified in the essential oil of L. camara [105,134,138,188]. These observations suggest that β-caryophyllene in the extracts of L. camara may cause oxidative stress conditions, and interrupt ROS extinction, resulting in the necrosis of the neighboring competitive plant species.
These observations suggest that L. camara is allelopathic and produces and releases certain allelochemicals into the neighboring environments, including its rhizosphere soil. These released allelochemicals suppress the germination, growth, and/or development of the competitive plant species. According to the novel weapon hypothesis, the allelochemicals released from the invasive plant species are more effective in the introduced ranges than in the native ranges of the invasive plant species. The plant species in the native ranges of the invasive plant species may have obtained the ability to cope with the inhibitory effects of these allelochemicals during their co-evolutional history. However, the competitive plant species in their introduced ranges may not have an opportunity to obtain the tolerance because they have not been existing together [159,160]. Therefore, allelochemicals of L. camara may be effective in the introduced ranges and contribute the infestation and expanding the population of L. camara.

7. Contributions of the Compounds to the Invasive Characteristics of L. camara

L. camara produces several defensive compounds against the herbivore mammals and insects, parasitic nematodes, pathogenic fungi and bacteria, and allelochemicals against the neighboring competitive plant species. Among them, lantadene A and lantadene B showed hepatotoxic activity against herbivore mammals through the interruption of the hepatic microsome and mitochondrial functions [48,59,67,68]. Lantadene A also showed anti-fungal activity against the pathogenic fungi Fusarium spp. and allelopathic activity against Eichhornia crassipes and Microcystis aeruginosa [137,187].
L. camara emits β-caryophyllene and cis-3-hexen-1-ol upon herbivorous insect attacks, and these compounds may work as the HIPVs involved in the indirect defense functions: (1) chemical signals from damaged plant tissues to undamaged tissues and (2) attractions of the predator insects to hunt the herbivorous insects [95,96,97]. β-Caryophyllene also showed insecticidal activity and fungicidal activity [100,105,134]. Farnesol and farnesal may disturb the insect juvenile hormone biosynthesis and cause the abnormal metamorphosis of the insects [100,101,102,103,104].
Lantanolic acid, lantoic acid, pomolic acid, camarin, lantacin, camarinin, ursolic acid, and oleanonic acid showed nematocidal activity, increasing the mortality and suppressing the egg hatching of the nematodes [125,126,127,128]. Germacrene-D and β-curcumene suppressed the growth of pathogenic fungi [134,138]. β-Caryophyllene, α-curcumene, β-curcumene, γ-muurolene, caffeic acid, p-coumaric acid, ferulic acid, gentisic acid, salicylic acid, α-resorcylic acid, β-resorcylic acid, p-hydroxybenzoic acid, vanillic acid, vanillin, methyl coumarin, unbelliferone, quercetin, and vitexin may act as allelochemicals, causing the inhibition of the germination and growth of neighboring competitive plant species [188,189,193]. These compounds are summarized in Table 1, and the action mechanisms of some of the compounds for the defense functions and allelopathy are shown in Figure 8.
Phytochemical and pharmacological investigations showed that L. camara contains many other secondary metabolites in several chemical classes, such as monoterpenes, sesquiterpenes, triterpenes, and flavonoids. Some of these compounds have been reported to exhibit pharmacological activities, such as anticancer activity, anti-inflammatory activity, anti-viral activity, antipyretic activity, and wound-healing activity for medicinal treatments, anti-microbial activity for food security, and anti-mosquito activity [47,48,49,50,51,52,53,54]. Although these biological active compounds have not yet been connected to the invasive characteristics of L. camara, some of them may be involved in the invasive characteristics of L. camara regarding its unknown functions. Several authors have suggested that L. camara contains alkaloids [145,205,206]. They detected alkaloid in the extracts of L. camara using Harbore method or Mayer’s reagent, which make the precipitation of alkaloid [207,208]. Many alkaloids are toxic and act as defensive compounds for several plant species against herbivores and pathogenic fungi [209,210,211]. However, no specific alkaloid compound has been reported in L. camara.

8. Conclusions

L. camara has naturalized in many tropical, subtropical, and temperate regions as one of the world’s 100 worst invasive alien species. Its infestation reduces the species diversity and abundance in the natural ecosystems, as well as agricultural production. The life history characteristics of L. camara, such as its high reproductive ability and high adaptive ability to various environmental conditions, may contribute to its ability to infest and increase its population. In addition, L. camara produces several compounds involved in defense functions against their natural enemies, such as herbivore mammals and insects, parasitic nematodes, and pathogenic fungi and bacteria, as well as allelochemicals involved in the allelopathy against competitive plant species. Their defense functions against natural enemies, as well as allelopathy against the competitive plant species, are among the essential factors that are necessary for success in dealing with the infestation and expanding population. Therefore, these compounds may also contribute to the infestation and expansion of L. camara in the new habitats.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Kew Royal Botanical Gardens Kew. Lantana camara L. Available online: https://powo.science.kew.org/taxon/325686-2 (accessed on 20 December 2024).
  2. CABI Compendium. Lantana camara (Lantana). Available online: https://www.cabidigitallibrary.org/doi/full/10.1079/cabicompendium.29771 (accessed on 20 December 2024).
  3. Global Invasive Species Database. Species Profile: Lantana camara. Available online: http://www.iucngisd.org/gisd/species.php?sc=56 (accessed on 20 December 2024).
  4. Weeds Australia—Profiles Lantana camara L. Available online: https://weeds.org.au/profiles/lantana-common-kamara/ (accessed on 20 December 2024).
  5. Sharma, G.P.; Raghubanshi, A.S.; Singh, J.S. Lantana invasion: An overview. Weed Biol. Manag. 2005, 5, 157–165. [Google Scholar] [CrossRef]
  6. Priyanka, N.; Joshi, P.K. A review of Lantana camara studies in India. Int. J. Sci. Res. Publ. 2013, 3, 1–11. [Google Scholar]
  7. Bhagwat, S.A.; Breman, E.; Thekaekara, T.; Thornton, T.F.; Willis, K.J. A battle lost? Report on two centuries of invasion and management of Lantana camara L. in Australia, India and South Africa. PLoS ONE 2012, 7, e32407. [Google Scholar] [CrossRef] [PubMed]
  8. Day, M.D.; Zalucki, M.P. Lantana camara Linn. (Verbenaceae). In Biological Control of Tropical Weeds Using Arthropods; Reeder, M.M., Ed.; Cambridge University Press: Cambridge, UK, 2009; pp. 211–246. [Google Scholar]
  9. Sundaram, B.; Hiremath, A.J. Lantana camara invasion in a heterogeneous landscape: Patterns of spread and correlation with changes in native vegetation. Biol. Invasions 2012, 14, 1127–1141. [Google Scholar] [CrossRef]
  10. Negi, G.C.; Sharma, S.; Vishvakarma, S.C.; Samant, S.S.; Maikhuri, R.K.; Prasad, R.C.; Palni, L.M. Ecology and use of Lantana camara in India. Bot. Rev. 2019, 85, 109–130. [Google Scholar] [CrossRef]
  11. Vardien, W.; Richardson, D.M.; Foxcroft, L.C.; Thompson, G.D.; Wilson, J.R.U.; Le Roux, J.J. Invasion dynamics of Lantana camara L. (sensu lato) in South Africa. S. Afr. J. Bot. 2012, 81, 81–94. [Google Scholar] [CrossRef]
  12. Taylor, S.; Kumar, L.; Reid, N. Impacts of climate change and land-use on the potential distribution of an invasive weed: A case study of Lantana camara in Australia. Weed Res. 2012, 52, 391–401. [Google Scholar] [CrossRef]
  13. IUCN. 100 of the World’s Worst Invasive Alien Species. Available online: https://portals.iucn.org/library/sites/library/files/documents/2000-126.pdf (accessed on 20 December 2024).
  14. Adhikari, P.; Lee, Y.H.; Adhikari, P.; Poudel, A.; Choi, S.H.; Yun, J.Y.; Lee, D.H.; Park, Y.S.; Hong, S.H. Global invasion risk assessment of Lantana camara, a highly invasive weed, under future environmental change. Glob. Ecol. Conserv. 2024, 55, e03212. [Google Scholar] [CrossRef]
  15. Zhang, Q.; Zhang, Y.; Peng, S.; Zobel, K. Climate warming may facilitate invasion of the exotic shrub Lantana camara. PLoS ONE 2014, 9, e105500. [Google Scholar] [CrossRef] [PubMed]
  16. Chaudhary, A.; Sarkar, M.S.; Adhikari, B.S.; Rawat, G.S. Ageratina adenophora and Lantana camara in Kailash Sacred Landscape, India: Current distribution and future climatic scenarios through modeling. PLoS ONE 2021, 16, e0239690. [Google Scholar] [CrossRef]
  17. Kohli, R.K.; Dogra, K.S.; Batish, D.R.; Singh, H.P. Impact of invasive plants on the structure and composition of natural vegetation of northwestern Indian Himalayas. Weed Technol. 2004, 18, 1296–1300. [Google Scholar] [CrossRef]
  18. Dogra, K.S.; Kohli, R.K.; Sood, S.K. An assessment and impact of three invasive species in the Shivalik hills of Himachal Pradesh, India. Int. J. Biodivers. Conserv. 2009, 1, 4–10. [Google Scholar]
  19. Gooden, B.; French, K.; Turner, P.J. Invasion and management of a woody plant, Lantana camara L., alters vegetation diversity within wet sclerophyll forest in southeastern Australia. For. Ecol. Manag. 2009, 257, 960–967. [Google Scholar] [CrossRef]
  20. Paudel, C.K.; Tiwari, A.; Baniya, C.B.; Shrestha, B.B.; Jha, P.K. High impacts of invasive weed Lantana camara on plant community and soil physicochemical properties across habitat types in Central Nepal. Forests 2024, 15, 1427. [Google Scholar] [CrossRef]
  21. Iqbal, I.M.; Balzter, H.; Shabbir, A. Mapping Lantana camara and Leucaena leucocephala in protected areas of Pakistan: A geo-spatial approach. Remote Sens. 2023, 15, 1020. [Google Scholar] [CrossRef]
  22. Fandohan, A.B.; Koko, I.K.E.D.; Avocevou-Ayisso, C.; Gouwakinnou, G.N.; Savi, M.K.; Assogbadjo, A.E.; Kakai, R.G. Lantana camara (verbenaceae): A potential threat to the effectiveness of protected areas to conserve flora and fauna in Benin. Agron. Afr. 2015, 27, 115–126. [Google Scholar]
  23. Le Maitre, D.C.; Versfeld, D.B.; Chapman, R.A. The impact of invading alien plants on water resources in South Africa: A preliminary assessment. Water Res. Comm. 2000, 26, 397–408. [Google Scholar]
  24. Raphela, T.D.; Duffy, K. The Impact of Lantana camara on Invertebrates and plant species of the Groenkloof Nature Reserve, South Africa. Zool. Stud. 2002, 61, 33. [Google Scholar]
  25. Osunkoya, O.O.; Perrett, C. Lantana camara L. (Verbenaceae) invasion effects on soil physicochemical properties. Biol. Fertil. Soils 2011, 47, 349–355. [Google Scholar] [CrossRef]
  26. Ruwanza, S.; Shackleton, C.M. Effects of the invasive shrub, Lantana camara, on soil properties in the Eastern Cape, South Africa. Weed Biol. Manag. 2016, 16, 67–79. [Google Scholar] [CrossRef]
  27. te Beest, M.; Le Roux, J.J.; Richardson, D.M.; Brysting, A.K.; Suda, J.; Kubešová, M.; Pyšek, P. The more the better? The role of polyploidy in facilitating plant invasions. Ann. Bot. 2012, 109, 19–45. [Google Scholar] [CrossRef]
  28. Swarbrick, J.T.; Willson, B.W.; Hannan-Jones, M.A. The biology of Australian weeds 25. Lantana camara L. Plant Prot. Q. 1995, 10, 82. [Google Scholar]
  29. Samways, M.J.; Caldwell, P.M.; Osborn, R. Ground-living invertebrate assemblages in native, planted and invasive vegetation in South Africa. Agric. Ecosys. Environ. 1995, 59, 19–32. [Google Scholar] [CrossRef]
  30. Nanjappa, H.V.; Saravanane, P.; Ramachandrappa, B.K. Biology and management of Lantana camara L.—A review. Agric. Rev. 2005, 26, 272–280. [Google Scholar]
  31. Aravind, N.A.; Rao, D.; Ganeshaiah, K.N.; Shaanker, R.U.; Poulsen, J.G. Impact of the invasive plant, Lantana camara, on bird assemblages at Malé Mahadeshwara Reserve Forest, South India. Trop. Ecol. 2010, 51, 325–338. [Google Scholar]
  32. Raphela, T.D.; Duffy, K.J. Effects of the density of invasive Lantana camara plants on the biodiversity of large and small mammals in the Groenkloof Nature Reserve (GNR) in South Africa. Biology 2023, 12, 296. [Google Scholar] [CrossRef]
  33. Berry, Z.C.; Wevill, K.; Curran, T.J. The invasive weed Lantana camara increases fire risk in dry rainforest by altering fuel beds. Weed Res. 2011, 51, 525–533. [Google Scholar] [CrossRef]
  34. Shackleton, R.T.; Witt, A.B.; Aool, W.; Pratt, C.F. Distribution of the invasive alien weed, Lantana camara, and its ecological and livelihood impacts in eastern Africa. Afr. J. Range Forage Sci. 2017, 34, 1–11. [Google Scholar] [CrossRef]
  35. Kamath, M.K. A review of biological control of insect pests and noxious weeds in Fiji (1969–1978). Fiji Agric. J. 1979, 41, 55–72. [Google Scholar]
  36. Cock, M.J.W.; Godfray, H.C.J. Biological control of Lantana camara L. in the Philippines. J. Plant Prot. Trop. 1985, 2, 61–63. [Google Scholar]
  37. Habeck, D.H. The case for biological control of lantana in Florida citrus groves. Proc. Florida State Hortic. Soc. 1976, 89, 17–18. [Google Scholar]
  38. Holm, L.G.; Plucknett, D.L.; Pancho, J.V.; Herberger, J.P. A Geographic Atlas of World Weeds; Krieger Publishing Company: Malabar, FL, USA, 1991; pp. 1–391. [Google Scholar]
  39. Swarbrick, J.T.; Willson, B.W.; Hannan-Jones, M.A. Lantana camara L. In The Biology of Australian Weeds; Panetta, F.D., Groves, R.H., Shepherd, R.C.H., Eds.; R.G. and F.J. Richardson: Melbourne, Australia, 1998; pp. 119–140. [Google Scholar]
  40. Graaff, J.L. Lantana camara, the plant and some methods for its control. S. Afr. For. J. 1986, 136, 26–30. [Google Scholar] [CrossRef]
  41. Love, A.; Babu, S.; Babu, C.R. Management of Lantana, an invasive alien weed, in forest ecosystems of India. Curr. Sci. 2009, 97, 1421–1429. [Google Scholar]
  42. Gentle, C.B.; Duggin, J.A. Allelopathy as a competitive strategy in persistent thickets of Lantana camara L. in three Australian forest communities. Plant Ecol. 1997, 132, 85–95. [Google Scholar] [CrossRef]
  43. Ray, A.; Quader, S. Genetic diversity and population structure of Lantana camara in India indicates multiple introductions and gene flow. Plant Biol. 2014, 16, 651–658. [Google Scholar] [CrossRef]
  44. Goyal, N.; Sharma, G.P. Lantana camara L. (sensu lato): An enigmatic complex. NeoBiota 2015, 25, 15–26. [Google Scholar]
  45. Mack, R.N.; Simberloff, D.; Lonsdale, W.M.; Evans, H.; Clout, M.; Bazzaz, F.A. Biotic invasions: Causes, epidemology, global consequences and control. Ecol. Appl. 2000, 10, 689–710. [Google Scholar] [CrossRef]
  46. Ntalo, M.; Ravhuhali, K.E.; Moyo, B.; Hawu, O.; Msiza, N.H. Lantana camara: Poisonous species and a potential browse species for goats in Southern Africa—A review. Sustainability 2022, 14, 751. [Google Scholar] [CrossRef]
  47. Ghisalberti, E.L. Lantana camara L. (Verbenaceae). Fitoterapia 2000, 71, 467–486. [Google Scholar] [CrossRef] [PubMed]
  48. Sharma, O.P.; Sharma, S.; Pattabhi, V.; Mahato, S.B.; Sharma, P.D. A review of the hepatotoxic plant Lantana camara. Crit. Rev. Toxicol. 2007, 37, 313–352. [Google Scholar] [CrossRef]
  49. Sousa, E.O.; Costa, J.G. Genus Lantana: Chemical aspects and biological activities. Rev. Bras. Farmacogn. 2012, 22, 1115–1180. [Google Scholar] [CrossRef]
  50. Shah, M.; Alharby, H.F.; Hakeem, K.R. Lantana camara: A comprehensive review on phytochemistry, ethnopharmacology and essential oil composition. Lett. Appl. Nanobiosci. 2020, 9, 1199–1207. [Google Scholar]
  51. Kumar, R.; Guleria, N.; Deeksha, M.G.; Kumari, N.; Kumar, R.; Jha, A.K.; Parmar, N.; Ganguly, P.; de Aguiar Andrade, E.H.; Ferreira, O.O.; et al. From an invasive weed to an insecticidal agent: Exploring the potential of Lantana camara in insect management strategies—A review. Int. J. Mol. Sci. 2024, 25, 12788. [Google Scholar] [CrossRef]
  52. Khan, M.; Srivastava, S.K.; Syamasundar, K.V.; Singh, M.; Naqvi, A.A. Chemical composition of leaf and flower essential oil of Lantana camara from India. Flavour Fragr. J. 2002, 17, 75–77. [Google Scholar] [CrossRef]
  53. Kalita, S.; Kumar, G.; Karthik, L.; Rao, K.V.B. A review on medicinal properties of Lantana camara Linn. Res. J. Pharm. Technol. 2012, 5, 711–715. [Google Scholar]
  54. Reddy, N.M. Lantana camara Linn. Chemical constituents and medicinal properties: A review. Sch. Acad. J. Pharm. 2013, 2, 445–448. [Google Scholar]
  55. Quinn, J.C.; Kessell, A.; Weston, L.A. Secondary plant products causing photosensitization in grazing herbivores: Their structure, activity and regulation. Int. J. Mol. Sci. 2014, 15, 1441–1465. [Google Scholar] [CrossRef]
  56. Tokarnia, C.H.; Döbereiner, J.; Lazzari, A.A.; Peixoto, P.V. Intoxicação por Lantana spp. (Verbenaceae) em bovinos nos Estados de Mato Grosso e Rio de Janeiro. Pesq. Vet. Bras. 1984, 4, 129–141. [Google Scholar]
  57. Sharma, O.P.; Dawra, R.K.; Makkar, H.P.S. Effect of polymorphic crystal forms of lantana toxins on icterogenic action in guinea pigs. Toxicol. Lett. 1988, 42, 29–37. [Google Scholar] [CrossRef] [PubMed]
  58. Sharma, O.P.; Makkar, H.P.; Dawra, R.K. A review of the noxious plant Lantana camara. Toxicon 1988, 26, 975–987. [Google Scholar] [CrossRef] [PubMed]
  59. Machado, M.; Oliveira, L.G.; Schild, C.O.; Boabaid, F.; Lucas, M.; Buroni, F.; Castro, M.B.; Riet-Correa, F. Lantana camara poisoning in cattle that took refuge during a storm in a forest invaded by this plant. Toxicon 2023, 229, 107124. [Google Scholar] [CrossRef] [PubMed]
  60. Bevilacqua, A.H.V.; Suffredini, I.B.; Romoff, P.; Lago, J.H.G.; Bernardi, M.M. Toxicity of apolar and polar Lantana camara L. crude extracts in mice. Res. Vet. Sci. 2011, 90, 106–115. [Google Scholar] [CrossRef] [PubMed]
  61. Nellis, D.W. Poisonous Plants and Animals of Florida and the Caribbean; Pineapple Press Inc.: Sarasota, FL, USA, 1997; pp. 1–416. [Google Scholar]
  62. Sharma, S.; Sharma, O.P.; Singh, B.; Bhat, T.K. Biotransformation of lantadenes, the pentacyclic triterpenoid hepatotoxins of lantana plant, in guinea pig. Toxicon 2000, 38, 1191–1202. [Google Scholar] [CrossRef] [PubMed]
  63. Pattabhi, V.; Sukumar, N.; Sharma, O.P. Crystal structure of lantadene A, the major triterpenoid from Lantana camara, red variety. Acta Crystallogr. 1991, 47, 810–812. [Google Scholar]
  64. Ji Netha, M.; Rufes, C.; Sadasivan, C.; Pattabhi, V.; Sharma, O.P. Molecular structure of lantadene B & C, triterpenoids of Lantana camara, red variety: Lantadene B, 22β- angeloyloxy-3-oxoolean-12-en-28oic acid; lantadene C, 22β(S)-2-methylbutanoyloxy-3- oxoolean-12-en-28-oic acid. J. Crystallogr. Spectrosc. Res. 1993, 23, 469–472. [Google Scholar]
  65. Kabaleeswaran, V.; Rajan, S.S.; Pattabhi, V.; Sharma, O.P. Crystal structure of angeloyloxy-oleanolic acid (reduced lantadene A) C35H54O5. Z. Kristallogr. 1996, 211, 411–412. [Google Scholar] [CrossRef]
  66. Sharma, O.P.; Vaid, J.; Pattabhi, V.; Bhutani, K.K. Biological action of lantadene C, a new hepatotoxicant from Lantana camara var. aculeala. J. Biochem. Toxicol. 1992, 7, 73–79. [Google Scholar] [CrossRef]
  67. Sharma, O.P.; Dawra, R.K. Effect of lantana toxicity on canalicular plasma membrane of guinea pig liver. Chem. Biol. Interact. 1984, 49, 369–374. [Google Scholar] [CrossRef] [PubMed]
  68. Garcia, A.F.; Medeiros, H.C.; Maioli, M.A.; Lima, M.C.; Rocha, B.A.; da Costa, F.B.; Curti, C.; Groppo, M.; Mingatto, F.E. Comparative effects of lantadene A and its reduced metabolite on mitochondrial bioenergetics. Toxicon 2010, 55, 1331–1337. [Google Scholar] [CrossRef] [PubMed]
  69. Porter, A.G.; Jänicke, R.U. Emerging roles of caspase-3 in apoptosis. Cell Death Differ. 1999, 6, 99–104. [Google Scholar] [CrossRef] [PubMed]
  70. Gao, W.; Wang, X.; Zhou, Y.; Wang, X.; Yu, Y. Autophagy, ferroptosis, pyroptosis, and necroptosis in tumor immunotherapy. Signal Transduct. Target. Ther. 2022, 7, 196. [Google Scholar] [CrossRef] [PubMed]
  71. Keane, R.M.; Crawley, M.L. Exotic plant invasions and the enemy release hypothesis. Trends Ecol. Evol. 2002, 17, 164–170. [Google Scholar] [CrossRef]
  72. Blossey, B.; Notzold, R. Evolution of increased competitive ability in invasive nonindigenous plants—A hypothesis. J. Ecol. 1995, 83, 887–889. [Google Scholar] [CrossRef]
  73. Muller-Scharer, H.; Schaffner, U.; Steinger, T. Evolution in invasive plants: Implications for biological control. Trends Ecol. Evol. 2004, 19, 417–422. [Google Scholar] [CrossRef] [PubMed]
  74. Mack, R.M. Predicting the identity and fate of plant invaders: Emergent and emerging approaches. Biol. Conserv. 1996, 78, 107–121. [Google Scholar] [CrossRef]
  75. Chengxu, W.; Mingxing, Z.; Xuhui, C.; Bo, Q. Review on allelopathy of exotic invasive plants. Procedia Eng. 2011, 18, 240–246. [Google Scholar] [CrossRef]
  76. Kato-Noguchi, H.; Kato, M. Invasive Characteristics and Impacts of Ambrosia trifida. Agronomy 2024, 14, 2868. [Google Scholar] [CrossRef]
  77. Kato-Noguchi, H. The impact and invasive mechanisms of Pueraria montana var. lobata, one of the world’s worst alien species. Plants 2023, 12, 3066. [Google Scholar] [PubMed]
  78. Kato-Noguchi, H.; Kurniadie, D. The invasive mechanisms of the noxious alien plant species Bidens pilosa. Plants 2024, 13, 356. [Google Scholar] [CrossRef] [PubMed]
  79. Kato-Noguchi, H.; Kato, M. Invasive characteristics of Robinia pseudoacacia and its impacts on the species diversity. Diversity 2024, 16, 773. [Google Scholar] [CrossRef]
  80. Palmer, W.A.; Pullen, K.R. The phytophagous arthropods associated with Lantana camara, L. hirsuta, L. urticifolia, and L. urticoides (Verbenaceae) in North America. Biol. Control 1995, 5, 54–72. [Google Scholar] [CrossRef]
  81. Palmer, W.A.; Pullen, K.R. The host range of Falconia intermedia (Distant) (Hemiptera: Miridae): A potential biological control agent for Lantana camara L. (Verbenaceae). Proc. Entomol. Soc. Wash. 1998, 100, 633–635. [Google Scholar]
  82. Baars, J.R.; Urban, A.J.; Hill, M.P. Biology, host range, and risk assessment supporting release in Africa of Falconia intermedia (Heteroptera: Miridae), a new biocontrol agent for Lantana camara. Biol. Control 2003, 28, 282–292. [Google Scholar] [CrossRef]
  83. Day, M.D.; McAndrew, T.D. The biology and host range of Falconia intermedia (Distant) (Hemiptera: Miridae), a potential biological control agent for Lantana camara L. (Verbenaceae) in Australia. Biocontrol Sci. Technol. 2003, 13, 13–22. [Google Scholar] [CrossRef]
  84. Baars, J.R.; Neser, S. Past and present initiatives on the biological control of Lantana camara (Verbenaceae) in South Africa. Afr. Entomol. Mem. 1999, 1, 21–33. [Google Scholar]
  85. Heshula, L.U.P.; Hill, M.P. The effect of Lantana camara leaf quality on the performance of Falconia intermedia. BioControl 2011, 56, 925–933. [Google Scholar] [CrossRef]
  86. Heshula, L.U.P.; Hill, M.P. The effect of sap-sucking by Falconia intermedia (Hemiptera: Miridae) on the emission of volatile organic compounds from the leaves of Lantana camara varieties. Afr. Entomol. 2014, 22, 210–213. [Google Scholar] [CrossRef]
  87. Schoonhoven, L.M.; van Loon, J.J.A.; Dicke, M. Insect-Plant Biology, 2nd ed.; Oxford University Press: Oxford, UK, 2006; pp. 1–440. [Google Scholar]
  88. Gatehouse, J.A. Plant resistance towards insect herbivores: A dynamic interaction. New Phytol. 2002, 156, 145–169. [Google Scholar] [CrossRef]
  89. Southwood, S.R. Insects and the plant surface. In Plant Surfaces and Insects—An Overview; Juniper, B., Southwood, R., Eds.; Edward Arnold Press: London, UK, 1986; pp. 1–22. [Google Scholar]
  90. Barthlott, W.; Mail, M.; Bhushan, B.; Koch, K. Plant surfaces: Structures and functions for biomimetic innovations. Nano-Micro Lett. 2017, 9, 1–40. [Google Scholar] [CrossRef]
  91. Kollner, T.G.; Held, M.; Lenk, C.; Hiltpold, I.; Turlings, T.C.; Gershenzon, J.; Degenhardt, J. A maize (E)-β-caryophyllene synthase implicated in indirect defense responses against herbivores is not expressed in most American maize varieties. Plant Cell 2008, 20, 482–494. [Google Scholar] [CrossRef] [PubMed]
  92. Robert, C.A.; Erb, M.; Duployer, M.; Zwahlen, C.; Doyen, G.R.; Turlings, T.C. Herbivore-induced plant volatiles mediate host selection by a root herbivore. New Phytol. 2012, 194, 1061–1069. [Google Scholar] [CrossRef] [PubMed]
  93. Wang, Q.; Xin, Z.; Li, J.; Hu, L.; Lou, Y.; Lu, J. (E)-β-caryophyllene functions as a host location signal for the rice white-backed planthopper Sogatella furcifera. Physiol. Mol. Plant Pathol. 2015, 91, 106–112. [Google Scholar] [CrossRef]
  94. Khan, M.; Mahmood, A.; Alkhathlan, H.Z. Characterization of leaves and flowers volatile constituents of Lantana camara growing in central region of Saudi Arabia. Arab. J. Chem. 2016, 9, 764–774. [Google Scholar] [CrossRef]
  95. Aartsma, Y.; Bianchi, F.J.; van der Werf, W.; Poelman, E.H.; Dicke, M. Herbivore-induced plant volatiles and tritrophic interactions across spatial scales. New Phytol. 2017, 216, 1054–1063. [Google Scholar] [CrossRef]
  96. Dicke, M.; Baldwin, I.T. The evolutionary context for herbivore-induced plant volatiles: Beyond the ‘cry for help’. Trends Plant Sci. 2010, 15, 167–175. [Google Scholar] [CrossRef] [PubMed]
  97. Agawall, A.A. Future direction in the study of induced response to herbivory. Entomol. Exp. Appl. 2005, 115, 97–105. [Google Scholar] [CrossRef]
  98. Kasmara, H.; Melanie, M.; Nurfajri, D.A.; Hermawan, W.; Panatarani, C. The toxicity evaluation of prepared Lantana camara nano extract against Spodoptera litura (Lepidoptera: Noctuidae). In Proceedings of the 1st International Conference and Exhibition on Powder Technology, Jatinangor, Indonesia, 8–9 August 2017; AIP Publishing: Melville, NY, USA, 2017; p. 030046. [Google Scholar]
  99. Melanie, M.; Hermawan, W.; Kasmara, H.; Panatarani, C. Physicochemical characterizations and insecticidal properties of Lantana camara leaf ethanolic extract with powder application. In Proceedings of the 2nd International Conference and Exhibition on Powder Technology, Surakarta, Indonesia, 20–21 August 2019; AIP Publishing: Melville, NY, USA, 2020; p. 04002. [Google Scholar]
  100. Kayesth, S.; Gupta, K.K. Impact of Lantana camara hexane extract on survival, growth and development of Dysdercus koenigii Fabricius (Heteroptera: Pyrrhocoriedae). Acta Ecol. Sin. 2018, 38, 187–192. [Google Scholar] [CrossRef]
  101. Ganesan, T.; Subban, M.; Leslee, D.B.C.; Kuppannan, S.B.; Seedevi, P. Structural characterization of n-hexadecanoic acid from the leaves of Ipomoea eriocarpa and its antioxidant and antibacterial activities. Biomass Convers. Biorefin. 2024, 14, 14547–14558. [Google Scholar] [CrossRef]
  102. Belles, X.; Martin, D.; Piulachs, M.D. The mevalonate pathway and the synthesis of juvenile hormone in insects. Annu. Rev. Entomol. 2005, 50, 181–199. [Google Scholar] [CrossRef] [PubMed]
  103. Huang, J.; Marchal, E.; Hult, E.F.; Tobe, S.S. Characterization of the juvenile hormone pathway in the viviparous cockroach, Diploptera punctata. PLoS ONE 2015, 10, e0117291. [Google Scholar] [CrossRef] [PubMed]
  104. Kayesth, S.; Kumar, S.; Shazad, M.; Gupta, K.K. Effects of hexane extract of Lantana camara leaves on reproductive bioactivities of Dysdercus koenigii Fabricius (Heteroptera: Pyrrhocoreidae). Acta Ecol. Sin. 2020, 40, 247–253. [Google Scholar] [CrossRef]
  105. Nea, F.; Kambiré, D.A.; Genva, M.; Tanoh, E.A.; Wognin, E.L.; Martin, H.; Brostaux, Y.; Tomi, F.; Lognay, G.C.; Tonzibo, Z.F.; et al. Composition, seasonal variation, and biological activities of Lantana camara essential oils from Côte d’Ivoire. Molecules 2020, 25, 2400. [Google Scholar] [CrossRef]
  106. Ogunsina, O.O.; Oladimeji, M.O.; Lajide, L. Insecticidal action of hexane extracts of three plants against bean weevil, Callosobruchus maculatus (F.) and maize weevil, Sitophilus zeamais Motsch. J. Ecol. Nat. Environ. 2011, 3, 23–28. [Google Scholar]
  107. Ayalew, A.A. Insecticidal activity of Lantana camara extract oil on controlling maize grain weevils. Toxicol. Res. Appl. 2020, 4, 2397847320906491. [Google Scholar] [CrossRef]
  108. Zoubiri, S.; Baaliouamer, A. Chemical composition and insecticidal properties of Lantana camara L. leaf essential oils from Algeria. J. Essent. Oil Res. 2012, 24, 377–383. [Google Scholar] [CrossRef]
  109. Saxena, R.C.; Dixit, O.P.; Harshan, V. Insecticidal action of Lantana camara against Callosobruchus chinensis (Coleoptera: Bruchidae). J. Stored Prod. Res. 1992, 28, 279–281. [Google Scholar] [CrossRef]
  110. Aisha, K.; Visakh, N.U.; Pathrose, B.; Mori, N.; Baeshen, R.S.; Shawer, R. Extraction, chemical composition and insecticidal activities of Lantana camara Linn. leaf essential oils against Tribolium castaneum, Lasioderma serricorne and Callosobruchus chinensis. Molecules 2024, 29, 344. [Google Scholar] [CrossRef] [PubMed]
  111. Ding, W.; Hu, X.P. Antitermitic effect of the Lantana camara plant on subterranean termites (Isoptera: Rhinotermitidae). Insect Sci. 2010, 17, 427–433. [Google Scholar] [CrossRef]
  112. Mitchell, C.E.; Power, A.G. Release of invasive plants from fungal and viral pathogens. Nature 2003, 421, 625–627. [Google Scholar] [CrossRef]
  113. Lambert, K.; Bekal, S. Introduction to Plant-Parasitic Nematodes. The Plant Health Instructor. Available online: https://www.apsnet.org/edcenter/disandpath/nematode/intro/Pages/IntroNematodes.aspx (accessed on 20 December 2024).
  114. den Akker, S.E. Plant–nematode interactions. Curr. Opin. Plant Biol. 2021, 62, 102035. [Google Scholar]
  115. Pires, D.; Vicente, C.S.L.; Menéndez, E.; Faria, J.M.S.; Rusinque, L.; Camacho, M.J.; Inácio, M.L. The fight against plant-parasitic nematodes: Current status of bacterial and fungal biocontrol agents. Pathogens 2022, 11, 1178. [Google Scholar] [CrossRef] [PubMed]
  116. Akhter, G.; Zafar, A.; Khan, W.; Jamshed, M. In vitro nemato-toxic potential of some leaf extracts on juvenile mortality of Meloidogyne incognita race-3. Arch. Phytopathol. Plant Prot. 2018, 51, 399–407. [Google Scholar] [CrossRef]
  117. Seid, A.; Fininsa, C.; Mekete, T.; Decraemer, W.; Wesemael, W.M. Tomato (Solanum lycopersicum) and root-knot nematodes (Meloidogyne spp.)—A century-old battle. Nematology 2015, 17, 995–1009. [Google Scholar] [CrossRef]
  118. Sikandar, A.; Zhang, M.Y.; Wang, Y.Y.; Zhu, X.F.; Liu, X.Y.; Fan, H.Y.; Xuan, Y.H.; Chen, L.J.; Duan, Y.X. Meloidogyne incognita (root-knot nematode) a risk to agriculture. Appl. Ecol. Environ. Res. 2020, 18, 1. [Google Scholar] [CrossRef]
  119. Ahmad, F.; Rather, M.A.; Siddiqui, M.A. Nematicidal activity of leaf extracts from Lantana camara L. against Meloidogyne incognita (kofoid and white) Chitwood and its use to manage roots infection of Solanum melongena L. Braz. Arch. Biol. Technol. 2010, 53, 543–548. [Google Scholar] [CrossRef]
  120. Bordoloi, K.; Bhagawati, B.; Baruah, A.M.; Neog, P.P.; Kurulkar, U. Biochemical mechanism of Lantana camara leaf extracts in the management of Meloidogyne incognita on tomato. J. Pharm. Phytochem. 2021, 10, 2828–2834. [Google Scholar] [CrossRef]
  121. Ali, N.I.; Siddiqui, A.; Zaki, M.J.; Shaukat, S.S. Nematicidal potential of Lantana camara against Meloidogyne javanica in mungbean. Nematol. Mediterr. Nematol. Medit. 2001, 29, 99–102. [Google Scholar]
  122. Malahlela, M.; Thibane, V.S.; Mudau, F.N. Nematocidal activity of fermented extracts from Lantana camara plant parts against Meloidogyne javanica on tomato. Int. J. Veg. Sci. 2021, 27, 20–28. [Google Scholar] [CrossRef]
  123. Shaukat, S.S.; Siddiqui, I.A. Lantana camara in the soil changes the fungal community structure and reduces impact of Meloidogyne javanica on mungbean. Phytopathol. Mediterr. 2001, 40, 245–252. [Google Scholar]
  124. Shaukat, S.S.; Siddiqui, I.A.; Ali, N.I.; Ali, S.A.; Khan, G.H. Nematicidal and allelopathic responses of Lantana camara root extract. Phytopathol. Mediterr. 2003, 42, 71–78. [Google Scholar]
  125. Begum, S.; Wahab, A.; Siddiqui, B.S.; Qamar, F. Nematicidal constituents of the aerial parts of Lantana camara. J. Nat. Prod. 2000, 63, 765–767. [Google Scholar] [CrossRef] [PubMed]
  126. Begum, S.; Zehra, S.Q.; Siddiqui, B.S.; Fayyaz, S.; Ramzan, M. Pentacyclic triterpenoids from the aerial parts of Lantana camara and their nematicidal activity. Chem. Biodivers. 2008, 5, 1856–1866. [Google Scholar] [CrossRef]
  127. Qamar, F.; Begum, S.; Raza, S.M.; Wahab, A.; Siddiqui, B.S. Nematicidal natural products from the aerial parts of Lantana camara Linn. Nat. Prod. Res. 2005, 19, 609–613. [Google Scholar] [CrossRef] [PubMed]
  128. Begum, S.; Ayub, A.; Siddiqui, B.S.; Fayyaz, S.; Kazi, F. Nematicidal triterpenoids from Lantana camara. Chem. Biodivers. 2015, 12, 1435–1442. [Google Scholar] [CrossRef] [PubMed]
  129. Knogge, W. Fungal infection of plants. Plant Cell 1996, 8, 1711. [Google Scholar] [CrossRef] [PubMed]
  130. Ghabrial, S.A.; Suzuki, N. Viruses of plant pathogenic fungi. Annu. Rev. Phytopathol. 2009, 47, 353–384. [Google Scholar] [CrossRef] [PubMed]
  131. Doehlemann, G.; Ökmen, B.; Zhu, W.; Sharon, A. Plant pathogenic fungi. Microbiol. Spectr. 2017, 5, Funk-0023-2016. [Google Scholar] [CrossRef] [PubMed]
  132. Ma, L.J.; Geiser, D.M.; Proctor, R.H.; Rooney, A.P.; O’Donnell, K.; Trail, F.; Gardiner, D.M.; Manners, J.M.; Kazan, K. Fusarium pathogenomics. Annu. Rev. Microbiol. 2013, 67, 399–416. [Google Scholar] [CrossRef] [PubMed]
  133. Katoch, R.; Thakur, M.; Paul, Y.S. Antifungal activity of the essential oils of Chromolaena adenophorum, Ageratum conyzoides and Lantana camara. Indian Phytopathol. 2012, 65, 409–411. [Google Scholar]
  134. Chauhan, N.; Haider, S.Z.; Lohani, H.; Godbole, S.; Gwari, G.; Bhandari, U. Chemical composition and antifungal activity of essential oil of Cymbopogon distans (Nees ex Steud.) W. Watson, Eupatorium adenophorum Spreng and Lantana camara L. grown in Uttarakhand (India). J. Biol. Act. Prod. Nat. 2015, 5, 234–240. [Google Scholar]
  135. Bansal, R.K.; Gupta, R.K. Evaluation of plant extracts against Fusarium oxysporum, wilt pathogen of fenugreek. Indian Phytopathol. 2000, 53, 107–108. [Google Scholar]
  136. Sharma, B.; Kumar, P. In vitro antifungal potency of some plant extracts against Fusarium oxysporum. Int. J. Green Pharm. 2009, 3, 63–65. [Google Scholar] [CrossRef]
  137. Seepe, H.A.; Raphoko, L.; Amoo, S.O.; Nxumalo, W. Lantadene A and boswellic acid isolated from the leaves of Lantana camara L. have the potential to control phytopathogenic Fusarium species. Heliyon 2022, 8, e12216. [Google Scholar] [CrossRef]
  138. Passos, J.L.; Barbosa, L.C.A.; Demuner, A.J.; Alvarenga, E.S.; da Silva, C.M.; Barreto, R.W. Chemical characterization of volatile compounds of Lantana camara L. and L. radula Sw. and their antifungal activity. Molecules 2012, 17, 11447–11455. [Google Scholar] [CrossRef] [PubMed]
  139. Silva, W.P.K.; Deverall, B.J.; Lyon, B.R. Molecular, physiological and pathological characterization of Corynespora leaf spot fungi rubber plantations in Sri Lanka. Plant Pathol. 1998, 47, 267–277. [Google Scholar] [CrossRef]
  140. Pereira, J.M.; Barreto, R.W.; Ellison, C.A.; Maffia, L.A. Corynespora cassiicola f. sp. lantanae: A potential biocontrol agent from Brazil for Lantana camara. Biol. Control 2003, 26, 21–31. [Google Scholar]
  141. Passos, J.L.; Barbosa, L.C.A.; Demuner, A.J.; King-Diaz, B.; Lotina-Hennsen, B. Effects of Corynespora cassiicola on Lantana camara. Planta Daninha 2010, 28, 229–237. [Google Scholar] [CrossRef]
  142. Ajayi-Oyetunde, O.O.; Bradley, C.A. Rhizoctonia solani: Taxonomy, population biology and management of rhizoctonia seedling disease of soybean. Plant Pathol. 2018, 67, 3–17. [Google Scholar] [CrossRef]
  143. Huang, B.; Du, J.; Huang, J.; Zhang, C.; He, H.; Guo, Z.; Yang, D.; Zheng, J.; Liu, Q. First report of Agroathelia rolfsii causing southern blight on cowpea in China. Plant Dis. 2024, 108, 811. [Google Scholar] [CrossRef]
  144. Humpherson-Jones, F.M.; Phelps, K. Climatic factors influencing spore production in Alternaria brassicae and Alternaria brassicicola. Ann. Appl. Biol. 1989, 114, 449–458. [Google Scholar] [CrossRef]
  145. Mansoori, A.; Singh, N.; Dubey, S.K.; Thakur, T.K.; Alkan, N.; Das, S.N.; Kumar, A. Phytochemical characterization and assessment of crude extracts from Lantana camara L. for antioxidant and antimicrobial activity. Front. Agron. 2020, 2, 582268. [Google Scholar] [CrossRef]
  146. Mhedbi-Hajri, N.; Hajri, A.; Boureau, T.; Darrasse, A.; Durand, K.; Brin, C.; Saux, M.S.L.; Manceau, C.; Poussier, S.; Pruvost, O.; et al. Evolutionary history of the plant pathogenic bacterium Xanthomonas axonopodis. PLoS ONE 2013, 8, e58474. [Google Scholar] [CrossRef] [PubMed]
  147. Wang, R.; Quan, G.; Kang, X.; Zhang, J.; Qin, Z. Influence of Lantana camara on soil. Effects on soil chemical properties, enzymes, and microorganisms. Allelopathy J. 2015, 35, 197–206. [Google Scholar]
  148. Gola, U.; Kour, S.; Kaur, T.; Perveen, K.; Bukhari, N.A.; Alsulami, J.A.; Maithani, D.; Dasila, H.; Singh, M.; Suyal, D.C. Prokaryotic diversity and community structure in the rhizosphere of Lantana weed (Lantana camara L.). Front. Plant Sci. 2023, 14, 1174859. [Google Scholar] [CrossRef]
  149. Kato-Noguchi, H. Allelopathy and allelochemicals of Imperata cylindrica as an invasive plant species. Plants 2022, 11, 2551. [Google Scholar] [CrossRef] [PubMed]
  150. Kato-Noguchi, H. Invasive mechanisms of one of the world’s worst alien plant species Mimosa pigra and its management. Plants 2023, 12, 1960. [Google Scholar] [CrossRef] [PubMed]
  151. Kato-Noguchi, H.; Kato, M. Evolution of the secondary metabolites in invasive plant species Chromolaena odorata for the defense and allelopathic functions. Plants 2023, 12, 521. [Google Scholar] [CrossRef] [PubMed]
  152. Kato-Noguchi, H. Allelopathy of knotweeds as invasive plants. Plants 2022, 11, 3. [Google Scholar] [CrossRef] [PubMed]
  153. Kato-Noguchi, H.; Kato, M. Defense molecules of the invasive plant species Ageratum conyzoides. Molecules 2024, 29, 4673. [Google Scholar] [CrossRef] [PubMed]
  154. Kato-Noguchi, H. Defensive molecules momilactones A and B: Function, biosynthesis, induction and occurrence. Toxins 2023, 15, 241. [Google Scholar] [CrossRef] [PubMed]
  155. Kato-Noguchi, H. Bioactive compounds involved in the formation of the sparse understory vegetation in pine forests. Curr. Org. Chem. 2021, 25, 1731–1738. [Google Scholar] [CrossRef]
  156. Rice, E.L. Allelopathy, 2nd ed.; Academic Press: Orlando, FL, USA, 1984; pp. 1–422. [Google Scholar]
  157. Bais, H.P.; Weir, T.L.; Perry, L.G.; Gilroy, S.; Vivanco, J.M. The role of root exudates in rhizosphere interactions with plants and other organisms. Annu. Rev. Plant Biol. 2006, 57, 233–266. [Google Scholar] [CrossRef] [PubMed]
  158. Kato-Noguchi, H. Isolation and identification of allelochemicals and their activities and functions. J. Pestic. Sci. 2024, 49, 1–14. [Google Scholar] [CrossRef] [PubMed]
  159. Callaway, R.M.; Ridenour, W.M. Novel weapons: Invasive success and the evolution of increased competitive ability. Front. Ecol. Environ. 2004, 2, 419–426. [Google Scholar] [CrossRef]
  160. Cappuccino, N.; Arnason, J.T. Novel chemistry of invasive exotic plants. Biol. Lett. 2006, 2, 189–193. [Google Scholar] [CrossRef] [PubMed]
  161. Kato-Noguchi, H. Involvement of allelopathy in the invasive potential of Tithonia diversifolia. Plants 2020, 9, 766. [Google Scholar] [CrossRef] [PubMed]
  162. Belz, R.G. Allelopathy in crop/weed interactions—An update. Pest. Manag. Sci. 2007, 63, 308–326. [Google Scholar] [CrossRef] [PubMed]
  163. Macías, F.A.; Molinillo, J.M.; Varela, R.M.; Galindo, J.C. Allelopathy—A natural alternative for weed control. Pest Manag. Sci. 2007, 63, 327–348. [Google Scholar] [CrossRef] [PubMed]
  164. Kato-Noguchi, H.; Saito, Y.; Suenaga, K. Involvement of allelopathy in the establishment of pure colony of Dicranopteris linearis. Plant Ecol. 2012, 213, 1937–1944. [Google Scholar] [CrossRef]
  165. Kato-Noguchi, H.; Saito, Y.; Ohno, O.; Suenaga, K. A phytotoxic active substance in the decomposing litter of the fern Gleichenia japonica. J. Plant Physiol. 2015, 176, 55–60. [Google Scholar] [CrossRef] [PubMed]
  166. Kato-Noguchi, H.; Kimura, F.; Ohno, O.; Suenaga, K. Involvement of allelopathy in inhibition of understory growth in red pine forests. J. Plant Physiol. 2017, 218, 66–73. [Google Scholar] [CrossRef] [PubMed]
  167. Kato-Noguchi, H. Phytotoxic Substances Involved in Teak Allelopathy and Agroforestry. Appl. Sci. 2021, 11, 3314. [Google Scholar] [CrossRef]
  168. Clements, D.R.; Kato-Noguchi, H. Defensive mechanisms of Mikania micrantha likely enhance its invasiveness as one of the world’s worst alien species. Plants 2025, 14, 269. [Google Scholar] [CrossRef]
  169. Ahmed, R.; Uddin, M.B.; Khan, M.A.; Mukul, S.A.; Hossain, M.K. Allelopathic effects of Lantana camara on germination and growth behavior of some agricultural crops in Bangladesh. J. For. Res. 2007, 18, 301–304. [Google Scholar] [CrossRef]
  170. Alemayehu, Y.; Chimdesa, M.; Yusuf, Z. Allelopathic effects of Lantana camara L. leaf aqueous extracts on germination and seedling growth of Capsicum annuum L. and Daucus carota L. Scientifica 2024, 2024, 9557081. [Google Scholar] [CrossRef]
  171. Zheng, H.Q.; Wei, N.; Wang, L.; He, P. Effects of Lantana camara leaf extract on the activity of superoxide dismutase and accumulation of H2O2 in water hyacinth leaf. J. Plant Physiol. Mol. Biol. 2006, 32, 189–194. [Google Scholar]
  172. Choyal, R.; Sharma, S.K. Allelopathic effects of Lantana camara (Linn) on Regeneration in Funaria hygrometrica. Indian J. Fundam. Appl. Life Sci. 2011, 1, 177–182. [Google Scholar]
  173. Achhireddy, N.R.; Singh, M.; Achhireddy, L.L.; Nigg, H.N.; Nagy, S. Isolation and partial characterization of phytotoxic compounds from lantana (Lantana camara L.). J. Chem. Ecol. 1985, 11, 979–988. [Google Scholar] [CrossRef] [PubMed]
  174. Maiti, P.P.; Bhakat, R.K.; Bhattacharjee, A. Allelopathic effects of Lantana camara on physio-biochemical parameters of Mimosa pudica seeds. Allelopath. J. 2008, 22, 59–67. [Google Scholar]
  175. Maiti, P. Biometric evaluation of allelopathic potential of Lantana camara L. on Mimosa seeds. J. Crit. Rev. 2020, 7, 837–847. [Google Scholar]
  176. Hussain, F.; Ghulam, S.; Sher, Z.; Ahmad, B. Allelopathy by Lantana camara L. Pak. J. Bot. 2011, 43, 2373–2378. [Google Scholar]
  177. Oudhia, P. Allelopathic effects of root leachates of some obnoxious weeds on germination and seedling vigour of wheat. Ecol. Environ. Conserv. 2001, 7, 111–113. [Google Scholar]
  178. Joshi, V.; Joshi, C.; Bargali, S.S.; Bargali, K. Effects of aqueous leachates from above ground parts of Lantana camara on seed germination, growth and yield of wheat crop. Ecol. Front. 2024, 44, 1241–1250. [Google Scholar] [CrossRef]
  179. Romero-Romero, T.; Anaya, A.L.; Cruz-Ortega, R. Screening for effects of phytochemical variability on cytoplasmic protein synthesis pattern of crop plants. J. Chem. Ecol. 2002, 28, 617–629. [Google Scholar] [CrossRef] [PubMed]
  180. Saxena, M.K. Aqueous leachate of Lantana camara kills water hyacinth. J. Chem. Ecol. 2000, 26, 2435–2447. [Google Scholar] [CrossRef]
  181. Motwani, G.; Golani, N.; Solanki, H. Allelopathic effects of aqueous leaf leachates of Lantana camara on Eichhorina crassipes. Life Sci. Leafl. 2013, 1, 83–90. [Google Scholar]
  182. Mersie, W.; Singh, M. Allelopathic effect of lantana on some agronomic crops and weeds. Plant Soil 1987, 98, 25–30. [Google Scholar] [CrossRef]
  183. Achhireddy, N.R.; Singh, M. Allelopathic effects of lantana (Lantana camara) on milkweedvine (Morrenia odorata). Weed Sci. 1984, 32, 757–761. [Google Scholar] [CrossRef]
  184. Wang, R.; Kang, X.; Quan, G.; Zhang, J. Influence of Lantana camara on soil II. Effects of Lantana camara leaf litter on plants and soil properties. Allelopath. J. 2015, 35, 207–216. [Google Scholar]
  185. Singh, H.P.; Batish, D.R.; Dogra, K.S.; Kaur, S.; Kohli, R.K.; Negi, A. Negative effect of litter of invasive weed Lantana camara on structure and composition of vegetation in the lower Siwalik Hills, northern India. Environ. Monit. Assess. 2014, 186, 3379–3389. [Google Scholar] [CrossRef]
  186. Hayyat, M.S.; Safdar, M.E.; Asif, M.; Tanveer, A.; Ali, L.; Qamar, R.; Ali, H.H.; Farooq, N.; Javeed, H.M.A.; Tarar, Z.H. Allelopathic effect of waste-land weeds on germination and growth of winter crops. Planta Daninha 2020, 38, e020173626. [Google Scholar] [CrossRef]
  187. Kong, C.H.; Wang, P.; Zhang, C.X.; Zhang, M.X.; Hu, F. Herbicidal potential of allelochemicals from Lantana camara against Eichhornia crassipes and the alga Microcystis aeruginosa. Weed Res. 2006, 46, 290–295. [Google Scholar] [CrossRef]
  188. Verdeguer, M.; Blázquez, M.A.; Boira, H. Phytotoxic effects of Lantana camara, Eucalyptus camaldulensis and Eriocephalus africanus essential oils in weeds of Mediterranean summer crops. Biochem. Syst. Ecol. 2009, 37, 362–369. [Google Scholar] [CrossRef]
  189. Singh, M.; Tamma, R.V.; Nigg, H.N. HPLC identification of allelopathic compounds from Lantana camara. J. Chem. Ecol. 1989, 15, 81–89. [Google Scholar] [CrossRef]
  190. Parvez, M.M.K.; Yokotani, T.; Fujii, Y.; Konishi, T.; Iwashina, T. Effects of quercetin and its seven derivatives on the growth of Arabidopsis thaliana and Neurospora crassa. Biochem. Syst. Ecol. 2004, 32, 631–635. [Google Scholar] [CrossRef]
  191. Okada, S.; Iwasaki, A.; Kataoka, I.; Suenaga, K.; Kato-Noguchi, H. Isolation and identification of a phytotoxic substance in kiwifruit leaves. Acta Hortic. 2018, 1218, 207–212. [Google Scholar] [CrossRef]
  192. Fernández-Aparicio, M.; Masi, M.; Cimmino, A.; Vilariño, S.; Evidente, A. Allelopathic effect of quercetin, a flavonoid from Fagopyrum esculentum roots in the radicle growth of Phelipanche ramosa: Quercetin natural and semisynthetic analogues were used for a structure-activity relationship investigation. Plants 2021, 10, 543. [Google Scholar] [CrossRef] [PubMed]
  193. Qureshi, H.; Anwar, T.; Ali, Q.; Haider, M.Z.; Habib, N.; Fatima, S.; Waseem, M.; Bibi, Y.; Arshad, M.; Adkins, S.W. Isolation of natural herbicidal compound from Lantana camara. Int. J. Environ. Anal. Chem. 2021, 101, 631–638. [Google Scholar] [CrossRef]
  194. Inderjit. Plant phenolics in allelopathy. Bot. Rev. 1996, 62, 186–202. [Google Scholar] [CrossRef]
  195. Einhellig, F.A. Mode of action of allelochemical action of phenolic compounds. In Chemistry and Mode of Action of Allelochemicals; Macías, F.A., Galindo, J.C.G., Molino, J.M.G., Cutler, H.G., Eds.; CRC Press: Boca Raton, FL, USA, 2004; pp. 217–238. [Google Scholar]
  196. Dalton, B.R. The occurrence and behavior of plant phenolic acids in soil environments and their potential involvement in allelochemical interference interactions: Methodological limitations in establishing conclusive proof of allelopathy. In Principals and Practices in Plant Ecology: Allelochemical Interactions; Inderjit, Dakshini, K.M.M., Foy, C.L., Eds.; CRC Press: Boca Raton, FL, USA, 1999; pp. 57–74. [Google Scholar]
  197. Moreland, D.E.; Novitzky, W.P. Effects of phenolic acids, coumarins, and flavonoids on isolated chloroplasts and mitochondria. In Allelochemicals: Role in Agriculture and Forestry; Waller, E.D., Ed.; Series 330; ACS Publications: Washington, DC, USA, 1987; pp. 247–274. [Google Scholar]
  198. Einhellig, F.A. Mechanisms of action of allelochemicals in allelopathy. In Allelopathy; Inderjit, Dakshini, K.M.M., Einhellig, F.A., Eds.; Series 582; ACS Publications: Washington, DC, USA, 1995; pp. 96–116. [Google Scholar]
  199. Li, Z.H.; Wang, Q.; Ruan, X.; Pan, C.D.; Jiang, D.A. Phenolics and plant allelopathy. Molecules 2010, 15, 8933–8952. [Google Scholar] [CrossRef] [PubMed]
  200. Widhalm, J.R.; Dudareva, N. A familiar ring to it: Biosynthesis of plant benzoic acids. Mol. Plant 2015, 8, 83–97. [Google Scholar] [CrossRef] [PubMed]
  201. Perry, J.J.P.; Shin, D.S.; Getzoff, E.D.; Tainer, J.A. The structural biochemistry of the superoxide dismutases. Biochim. Biophys. Acta 2010, 1804, 245–262. [Google Scholar] [CrossRef]
  202. Miao, L.; Clair, D.K.S. Regulation of superoxide dismutase genes: Implications in disease. Free Radic. Biol. Med. 2009, 47, 344–356. [Google Scholar] [CrossRef] [PubMed]
  203. Heck, D.E.; Shakarjian, M.; Kim, H.D.; Laskin, J.D.; Vetrano, A.M. Mechanisms of oxidant generation by catalase. Ann. N. Y. Acad. Sci. 2010, 1203, 120–125. [Google Scholar] [CrossRef] [PubMed]
  204. Wang, R.; Peng, S.L.; Zeng, R.S.; Ding, L.W.; Xu, Z.F. Cloning, expression and wounding induction of β-caryophyllene synthase gene from Mikania micrantha HBK and allelopathic potential of β-caryophyllene. Allelopath. J. 2009, 24, 35–44. [Google Scholar]
  205. Gabi, B.; Adewumi, A.A.J.; Aina, V.O. Phytochemical characterization and in-vivo anti-malaria activity of Lantana camara leaf extract. Br. J. Pharmacol. Toxicol. 2011, 2, 277–282. [Google Scholar]
  206. Bhuvaneswari, E.; Giri, R.S. Physicochemical and phytochemical screening in Lantana camara leaves. J. Pharmacogn. Phytochem. 2018, 7, 1962–1966. [Google Scholar]
  207. Harborne, J.B. Phytochemical Methods a Guide to Modern Techniques of Plant Analysis, 3rd ed.; Chapman & Hall: London, UK, 1998; pp. 1–301. [Google Scholar]
  208. Massingill, J.L., Jr.; Hodgkins, J.E. Alkaloids of bacteria. Phytochemistry 1967, 6, 977–982. [Google Scholar] [CrossRef]
  209. Cushnie, T.T.; Cushnie, B.; Lamb, A.J. Alkaloids: An overview of their antibacterial, antibiotic-enhancing and antivirulence activities. Int. J. Antimicrob. Agents 2014, 44, 377–386. [Google Scholar] [CrossRef] [PubMed]
  210. Matsuura, H.N.; Fett-Neto, A.G. Plant alkaloids: Main features, toxicity, and mechanisms of action. Plant Toxins 2015, 2, 1–15. [Google Scholar]
  211. Thawabteh, A.M.; Thawabteh, A.; Lelario, F.; Bufo, S.A.; Scrano, L. Classification, toxicity and bioactivity of natural diterpenoid alkaloids. Molecules 2021, 26, 4103. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Stand and leaves of L. camara.
Figure 1. Stand and leaves of L. camara.
Molecules 30 00411 g001
Figure 2. Flowers and fruits of L. camara.
Figure 2. Flowers and fruits of L. camara.
Molecules 30 00411 g002
Figure 3. The compounds involved in the defense function against herbivore mammals.
Figure 3. The compounds involved in the defense function against herbivore mammals.
Molecules 30 00411 g003
Figure 4. The compounds involved in the defense function against herbivorous insects.
Figure 4. The compounds involved in the defense function against herbivorous insects.
Molecules 30 00411 g004
Figure 5. The compounds involved in the defense function against parasitic nematodes.
Figure 5. The compounds involved in the defense function against parasitic nematodes.
Molecules 30 00411 g005
Figure 6. The compounds involved in the defense function against pathogenic fungi and bacteria.
Figure 6. The compounds involved in the defense function against pathogenic fungi and bacteria.
Molecules 30 00411 g006
Figure 7. The compounds involved in the allelopathy.
Figure 7. The compounds involved in the allelopathy.
Molecules 30 00411 g007
Figure 8. Action mechanisms of the compounds discussed in this paper. These compounds are involved in the hepathoxic, insecticidal, nematocidal, fungicidal, and allelopathic activity of L. camara. Purple arrow: direct action; blue arrow: secondary and tertiary action.
Figure 8. Action mechanisms of the compounds discussed in this paper. These compounds are involved in the hepathoxic, insecticidal, nematocidal, fungicidal, and allelopathic activity of L. camara. Purple arrow: direct action; blue arrow: secondary and tertiary action.
Molecules 30 00411 g008
Table 1. Compounds involved in the defense functions against natural enemies, such as herbivore mammals and insects, parasitic nematodes, and pathogenic fungi and bacteria, as well as allelochemicals involved in the allelopathy.
Table 1. Compounds involved in the defense functions against natural enemies, such as herbivore mammals and insects, parasitic nematodes, and pathogenic fungi and bacteria, as well as allelochemicals involved in the allelopathy.
Defense Function AgainstAllelopathyReference
Phytochemical ClassCompoundMammalInsectNematodeFungus, BacteriumCompetitive Plant
TriterpeneLamtidines A e.g., [59,62,68,134,187]
Reduced lantadene A [62,68]
Lantadene B [58,62,187]
Reduced lantadene B [62]
Lantadene C [59]
Lantadene D [59]
Icterogenin [59]
Oleanonic acid [59,127,128]
Lantanolic acid [125,126]
Lantoic acid [125,126]
Pomolic acid [125,126]
Ursolic acid [125,126]
Camarinin [125,126]
Camarin [125,126]
Lantacin [125,126]
Sesquiterpeneβ-Caryophyllene [86,100,105,134,188]
β-Humulene [105]
Isoledene [110]
α-Copaene [110]
Farnesol [100]
Farnesal [100]
Germacrene-D [134,138]
β-Curcumene [134]
α-Curcumene [188]
γ-Muurolene [188]
MonoterpeneThymol [105]
Loliolide [145]
Aromatic compoundMethyl coumarin [189]
Unbelliferone [189]
Phenolic acidSalicylic acid [189]
Gentisic acid [189]
p-Hydroxybenzoic acid [189]
Vanillic acid [189]
α-Resorcylic acid [189]
β-Resorcylic acid [189]
Phenolic aldehydeVanillin [189]
PhenylpropanoidCaffeic acid [189]
p-Coumaric acid [189]
Ferulic acid [189]
FlavonoidQuercetin [189]
Flavone glucosideVitexin [193]
Alcoholcis-3-Hexen-1-ol [94]
Fatty acidHexadecanoic acid [100]
Eicosapentaenoic acid [145]
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Kato-Noguchi, H.; Kato, M. Compounds Involved in the Invasive Characteristics of Lantana camara. Molecules 2025, 30, 411. https://doi.org/10.3390/molecules30020411

AMA Style

Kato-Noguchi H, Kato M. Compounds Involved in the Invasive Characteristics of Lantana camara. Molecules. 2025; 30(2):411. https://doi.org/10.3390/molecules30020411

Chicago/Turabian Style

Kato-Noguchi, Hisashi, and Midori Kato. 2025. "Compounds Involved in the Invasive Characteristics of Lantana camara" Molecules 30, no. 2: 411. https://doi.org/10.3390/molecules30020411

APA Style

Kato-Noguchi, H., & Kato, M. (2025). Compounds Involved in the Invasive Characteristics of Lantana camara. Molecules, 30(2), 411. https://doi.org/10.3390/molecules30020411

Article Metrics

Back to TopTop