Allelopathy and Allelochemicals of Imperata cylindrica as an Invasive Plant Species

Imperata cylindrica is native to Southeast Asia and East Africa and has become naturalized in humid tropics, subtropics and warmer temperate zones of the world. The species is one of the top ten worst weeds in the worlds and is listed among the world’s top 100 worst invasive alien species. It is an aggressive colonizer and forms large monospecific stands in several countries. Possible evidence of the allelopathy of I. cylindrica has been accumulated in the literature over three decades. The extracts, leachates, root exudates, decomposing residues and rhizosphere soil of I. cylindrica were found to suppress the germination and growth of several plant species, including woody plant species, and to reduce their rhizobium nodulation and mycorrhizal colonization. Several allelochemicals, such as fatty acids, terpenoids, simple phenolics, benzoic acids, phenolic acids, phenolic aldehydes, phenylpropanoids, flavonoids, quinones and alkaloids, were also found in the extracts, leachates, root exudates and/or growth medium of I. cylindrica. These observations suggest that allelochemicals may be synthesized in I. cylindrica and released into the rhizosphere soil and surrounding environments either by the leachates, root exudation or decomposition process of plant parts, and certain allelochemicals may contribute to the alteration of the microbial community, including rhizobia and mycorrhizal fungi, suppressing the regeneration process of native plant species through the inhibition of their germination and growth. Therefore, the allelopathy of I. cylindrica may support its invasiveness, naturalization and formation of large monospecific stands. This is the first review article focusing on the allelopathy of I. cylindrica.


Introduction
Imperata cylindrica (L.) Beauv., belonging to Poaceae, is a C 4 perennial rhizomatous grass species (Figure 1). This species has an extensive rhizome network. The rhizome development of I. cylindrica occurs 3-12 weeks after germination, beginning with downward growth. When the rhizome develops cataphylls, it grows horizontally, and the tip of the rhizome begins to turn upward between the fifth and sixth leaf stages. Then, a secondary shoot and rhizome arise from the apical bud and subapical bud of the first rhizome, respectively. The secondary rhizome produces the third shoot and rhizome, continuing the following shoot and rhizome formations [1][2][3][4][5]. It was reported that one plant produced 31 rhizomes in 10 months, with a total rhizome length of 12 m [6]. The shoots form loose to compact tufts. Several leaf sheaths are often tightly rolled together, forming a cylindrical culm. I. cylindrica is virtually stemless, except for the flowering stalks. The leaves are flat, slender (4-10 mm in wide) and linear-lanceolate  cm in length, depending on the growth condition), possessing serrated margins embedded with sharp silica crystals. Stomata are present on both surfaces of the leaves [7][8][9][10].
I. cylindrica is native to Southeast Asia and East Africa and has become naturalized in humid tropics, subtropics and warmer temperate zones of the world [1,[11][12][13][14]. The species is considered one of the top ten worst weeds in the world and is listed among the world's and other disturbing factors, such as a hurricane, the establishment of new populations arises from rhizome pieces. The regeneration of I. cylindrica can occur within a small amount of rhizomes-as much as 0.1 g [30]. I. cylindrica rhizomes are also very fertile [31]. It was estimated that I. cylindrica produces 6 tons of rhizome biomass per hectare, with more than 4.5 million shoots and 10 metric tons of leaf biomass [32]. Terry et al. [33] also estimated a rhizome biomass of 40 tons per hectare. Over the course of 6 weeks, rhizomes were reported to develop 350 shoots, covering an area of 4 m 2 [34]. The extensive growth of I. cylindrica results dense mats of rhizomes in the soil, forming thick monospecific patches [32,33] (Figure 1).
I. cylindrica is an excellent competitor for nutrients. Its ability to absorb phosphorus, nitrogen and potassium is higher than that of native pine savanna plants, including Pinus taeda L. [35][36][37]. The species was reported to reduce the availability of water and nitrogen in surrounding soil, suppressing the establishment of juvenile P. taeda by 50% [38].
I. cylindrica has also been reported to increase wildfire occurrence and maximum wildfire temperatures [39,40]. High-temperature fire increases the mortality of native  The characteristics of life history, such as high reproduction and growth rates, competitive ability and phenotypic plasticity, of the plants are important for the naturalization of invasive plants into non-native ranges [22][23][24][25]. I. cylindrica is also a prolific seed producer, although its flowering is variable, depending on the environmental conditions. The inflorescence of I. cylindrica is 10-20 cm in length, with approximately 400 spikelets, which are 3-6 cm in length and covered with short, white hairs [5,7,8]. (Figure 1). A single plant produces 500-3000 seeds, which are contained in the spikelets. The movement of the seeds was reported to generally span 15 m, traveled distances of as much as 24 km with the spikelets through wind dispersal [1,26,27]. The germination rate is 30-98%, depending on the conditions [8,28,29].
Vegetative reproduction maintains local stands of I. cylindrica and contributes to spread the plant in its vicinity. When rhizome pieces are dispersed by human activities and other disturbing factors, such as a hurricane, the establishment of new populations arises from rhizome pieces. The regeneration of I. cylindrica can occur within a small amount of rhizomes-as much as 0.1 g [30]. I. cylindrica rhizomes are also very fertile [31]. It was estimated that I. cylindrica produces 6 tons of rhizome biomass per hectare, with more than 4.5 million shoots and 10 metric tons of leaf biomass [32]. Terry et al. [33] also estimated a rhizome biomass of 40 tons per hectare. Over the course of 6 weeks, rhizomes were reported to develop 350 shoots, covering an area of 4 m 2 [34]. The extensive growth of I. cylindrica results dense mats of rhizomes in the soil, forming thick monospecific patches [32,33] ( Figure 1).
I. cylindrica is an excellent competitor for nutrients. Its ability to absorb phosphorus, nitrogen and potassium is higher than that of native pine savanna plants, including Pinus taeda L. [35][36][37]. The species was reported to reduce the availability of water and nitrogen in surrounding soil, suppressing the establishment of juvenile P. taeda by 50% [38].
I. cylindrica has also been reported to increase wildfire occurrence and maximum wildfire temperatures [39,40]. High-temperature fire increases the mortality of native herbaceous and juvenile woody plant spices. Because I. cylindrica allocates a significant amount of biomass (over 60%) in below-ground rhizomes, it is able to regenerate quickly from its rhizomes after fires [37,39,41,42]. Therefore, frequent intense fires may result in the conversion of native ecosystems of herbaceous and juvenile woody plants into I. cylindrica-dominated grasslands.
The phenotypic plasticity of I. cylindrica is high, and the species has adapted to a wide range of environmental conditions, such as various soil types, pH values (4.4 to 8.0), organic matter (0.9 to 5%) and nutrients (P; 6 to190 kg/ha, K; 46 to 734 kg/ha) [43]. It thrives in tropical, subtropical and warm temperate areas, where annual rainfall is 750-5000 mm [7]. Its characteristics in terms of floral traits (such as spikelets, anthers and glumes) and leaf traits (such as length and width) vary within the species [27,44,45]. The species can be separated into five major varieties based on growth and morphological characteristics, as well as geographic origin: I. cylindrica var. europa (2n = 40), major (2n = 20), Africana (2n = 60), latifolia (not available) and condensate (not available). The genetic diversity of I. cylindrica in 676 samples from seven southern US states was determined using amplified fragment length polymorphisms, with two genetic lineages identified [46]. Random amplified polymorphic DNA analysis conducted in Florida showed that the species was highly outcrossed [8]. Hybridization may have facilitated the expansion of the species.
The interactions of these invasive plants with natural enemies, such as herbivores and pathogens, are critical for their naturalization. [23,24,47]. Multiple insect predators and fungal pathogens have been identified in I. cylindrica stands. However, none of them caused the extensive damage to the population of I. cylindrica [21]. In addition, methanol extracts of shoots, roots and inflorescences of I. cylindrica showed antifungal activity against the plant pathogen Macrophomina phaseolina (Tassi) Goid. [48].
The chemical interactions of the invasive plants with native plants are also crucial [24,49,50]. Several observations suggest that some invasive plants are allelopathic and that their allelochemicals are toxic to native plant species in the invasive ranges [51,52]. Therefore, allelopathy may among the factors allowing the invasive plants to establish their habitats and naturalize within the invasive ranges [52]. Allelopathy is the chemical interaction between a donor plant and receiver plants through the specific secondary metabolites defined as allelochemicals [53]. Available data from a number of observations under field and laboratory conditions suggest that I. cylindrica is also allelopathic, and possible evidence for the compounds involved in this allelopathy has been accumulated. However, no review papers have been published focusing on the allelopathy of I. cylindrica. Therefore, in this review, we provide an overview of the allelopathy and allelochemicals of the I. cylindrica and discuss the possible involvement of allelopathy in the invasiveness of the species.

Effects of I. cylindrica on Microbial Community
Several investigations under field and greenhouse conditions have showed that I. cylindrica altered the microbial community in the rhizosphere soil and affected the growth of several plant species, including crop plants. The decomposition process of an I. cylindrica residue was reported to be significantly faster than that of a local native grass species, Andropogon glomeratus (Walt.) Britton, Sterns & Poggenb. I. cylindrica was reported to affect the microbial flora in the soil of invaded areas and enhance the decomposition process of the plant residue [54]. The enhanced decomposition process of the plant residue may enable increasing nutrient cycling and availability. Although there are many possible explanations for the alteration of the microbial community in the soil, certain compounds of I. cylindrica may be involved in this alteration.
The abundance of mycorrhizal colonization and biomass of fine feeder roots of Pinus taeda L. was significantly suppressed in I. cylindrica-infested plantations compared with plantations not infested by I. cylindrica. The diversity of understory vegetation in pine plantations was also reduced by the presence of I. cylindrica [55]. The invasion of I. cylindrica into a Pinus palustris Mill. community caused significant loss of native plant species and reduced the distinctiveness of the native flora [56]. Arbuscular mycorrhizal colonization of Mesicago denticulata Greene and Trifolium resupinatum L. was decreased in I. cylindrica-infested fields compared with non-infested fields [57]. The mycorrhizal colonization of some weed species was also suppressed by the presence of I. cylindrica [58]. In addition, the rhizobium nodulation, nitrogen fixation and root growth of Melilotus parviflora Desf. were suppressed when M. parviflora was grown together with I. cylindrica. The populations of some fungi, such as Aspergillus spp., also differed between I. cylindrica-infested soil and non-infested soil [59]. When I. cylindrica was grown with Zea mays L. or Sorghum bicolor (L.) Moench for 8 weeks, the biomass of I. cylindrica was not affected by the presence of Z. mays and S. bicolor. However, the biomass of Z. mays and S. bicolor was significantly reduced by the presence of I. cylindrica even under the conditions that eliminated possible nutrient competition [60]. These observations suggest that I. cylindrica may suppress the mycorrhizal colonization and rhizobium nodulation in native plant species, leading to the growth inhibition of these plant species. Although some authors found no direct evidence of allelopathy, they suggested the involvement of I. cylindrica allelopathy in the suppression of mycorrhizal colonization and rhizobium nodulation [54,[58][59][60].

Allelopathy of I. cylindrica
Allelochemicals are synthesized in certain plant parts and released into the vicinity of the plants either by rainfall leachates and volatilization from the plants, root exudation or decomposition of plant litter and residues [61][62][63]. The allelopathic activity of leachates, residues and plant extracts of I. cylindrica was evaluated over three decades (Table 1). Those observations suggest that I. cylindrica may synthesize some allelochemicals and release them into the neighboring environments either by rainfall leachates, exudation or the decomposition process of the plants.

Plant Leachates and Exudates
Water was sprinkled onto the chopped leaves of I. cylindrica as an artificial rain, and dripped water from the leaves was pumped up and sprinkled again onto the leaves. After 11 days of water circulation, dripped water was collected as artificial rainfall leachates and evaluated in terms of its allelopathic activity. The leachates suppressed the growth of Brachiaria mutica (Forssk.) Stapf and Digitaria decumbens Stent but not I. cylindrica itself [64]. Crushed dry shoots and roots of I. cylindrica were placed onto a large funnel containing a sheet of filter paper, which was kept in the open air and exposed to natural rainfall. Collected rainfall leachates from the crushed shoots and roots inhibited the germination of Dichanthium annulatum (Forssk.) Stapf and the radical growth of D. annulatum, Chrysopogon montanus Trin., Medicago polymorpha L. and Pinus roxburghii Sarg. [65].
I. cylindrica was grown in pots filled with a fine sand and irrigated with water twice a week, and drain water from holes at bottom of the pots was collected as I. cylindrica leachates. The leachates suppressed the aboveground biomass of Aristida stricta Michex. var. beyrichiana by 35.7%, its total root length by 24.9% and its mycorrhizal colonization by 23.5%. It also suppressed mycorrhizal colonization of Pinus elliottii Engelm by 19.5% [66]. The collected leachates may also contain its root exudates. I. cylindrica was grown in an agar medium for 7 day, and the medium was centrifuged after removing the plants. The resulting supernatant, which may contain root exudates of I. cylindrica, inhibited the roots and shoots growth of Echinochloa crus-galli (L.) Beauv. [67]. Soil obtained in I. cylindricadominated areas was extracted with water. The soil extracts inhibited the germination of Dichanthium annulatum (Forssk.) Stapf and Chrysopogon montanus Trin., as well as the radical growth of Setaria italica P. Beauv., D. annulatum, C. montanus, Medicago polymorpha L. and Pinus roxburghii Sarg. [65]. These observations suggest that the leachates and root exudates may contain allelochemicals, causing the growth inhibition and suppression of mycorrhizal colonization. These observations also imply that certain allelochemicals may be released from the leaves and below-ground parts of I. cylindrica into the rhizosphere soil or neighboring environments as plant leachates and exudates.

Plant Residues
The leaves of I. cylindrica were mixed with soil (0 g, 1.6 g and 3.2 g leaves per 100 g soil) in plastic trays (32 × 25 × 7 cm 3 ), and those trays were kept in a greenhouse with occasional watering. Weeds that emerged in the trays were identified, counted and removed every week for one year. There was no significant difference in the total number of emerged weeds among treatments. However, the total biomass of the weeds was 38.8%, and that of the control was 27.1% (0 g leaf) for the soil mixed with 1.6 g and 3.2 g leaves, respectively.
The predominant weed species were Erigeron canadensis L. and Portulaca oleracea L., which were also predominant weeds in the nearest experimental crop field [68].
Foliage or rhizomes and roots of I. cylindrica were mixed with sterilized sand medium, and the seeds of Sida spinosa L., Brachiaria ramosa (L.) Stapf., Echinochloa crus-galli (L.) Beauv., Cynodon dactylon (L.) Pers. and Lolium multiflorum Lam. were sown into the mixture and incubated for 10 days and 30 days to determine the rate of the germination and growth, respectively. All treatments resulted in the suppression of the germination of S. spinosa, B. ramosa, E. crus-galli, C. dactylon and L. multiflorum and the growth of S. spinosa, B. ramosa and E. crus-galli [69]. Whole plants of I. cylindrica were cut and mixed with a sand-peat medium. Rice seeds were then sown into the medium and incubated for 38 days. The treatments resulted in a reduction in the growth of Oryza sativa L. and the concentration of nitrogen and phosphate in rice seedlings [70].
Tillers, roots or rhizomes of I. cylindrica were incorporated into a soil mixture of sandy loam and sand and kept for 4 weeks. The I. cylindrica-incorporated soil mixtures were then extracted with water. The extracts of all soil mixtures inhibited the growth of Trifolium subterraneum L. radicles. However, the extract of the tiller mixture was the most effective [71]. These observations suggest that the whole plants, including leaves, roots and rhizomes, of I. cylindrica may contain certain allelochemicals, some of which may be released into the soil during the decomposition processes of plant residues.

Plant Extract
Because allelochemicals are synthesized and accumulated in some plant parts [61][62][63], many researchers have investigated the allelopathic activity of the extracts from different plant parts of I. cylindrica. Aqueous extracts of whole plants of I. cylindrica showed the inhibitory activity with respect to the germination of Oryza sativa L. [70]. Frequency and density of Parthenium hysterophorus L. was significantly lower in I. cylindrica-dominated areas than that in non-infested areas, and inhibition of the germination and seedling growth of P. hysterophorus was observed in association with treatments of the aqueous extracts of roots and shoots of I. cylindrica [72]. Aqueous extracts of roots and shoots of I. cylindrica also inhibited the germination and growth of Cucumis sativus L., Lolium perenne L. [73] and Centrosema pubescens Benth. [74].
Aqueous methanol extracts of I. cylindrica rhizomes inhibited the root and shoot growth of three monocotyledonous plants, Echinochloa crus-galli (L.) Beauv., Lolium multiflorum Lam. and Phleum pratense L., as well as that of three dicotyledonous plants, Lepidium sativum L., Lactuca sativa L. and Medicago sativa L. [78]. Leaf and rhizome powder of I. cylindrica was extracted with methanol, and the extract was concentrated. The concentrated extract was dissolved in water and sprayed onto the plant surface of Amaranthus spinosus L. The treatments resulted in a significant reduction in the growth of A. spinosus [79]. In addition, essential oil of roots and aerial parts of I. cylindrica suppressed the germination and seedlings of Lactuca sativa L. and Agrostis stolonifera L. [80].
Observations reported in this section suggest that the aqueous and methanol extracts of every part of I. cylindrica exhibit allelopathic activity with respect to the germination, growth, rhizobium nodulation and/or mycorrhizal colonization of several plant species and probably contain water-and methanol-extractable allelochemicals, which may cause the suppression of germination, growth, mycorrhizal colonization and/or rhizobium nodulation.

Allelochemicals of I. cylindrica
Many secondary metabolites were isolated and identified in the leachates, exudates and extracts of I. cylindrica, as well as its allelopathic agents ( Figure 2, Table 2). p-Hydroxybenzoic acid and p-coumaric acid were identified in artificial rainfall leachates from leaves of I. cylindrica [64]. Benzoic acid, salicylic acid, gallic acid, cinnamic acid, caffeic acid, sinapinic acid (sinapic acid), emodin and hexadecahydro-1-azachrysen-8-yl ester were identified in the drain water from the I. cylindrica growth medium. However, their concentrations were 0.6-18 µM [66], which may be lower than their biologically active concentrations.  Table 2.  Table 2.  Four compounds, palmitic acid, phytol, tabanone (4,6,8-megastigmatrien-3-one) and p-vinylguaiacol, were identified in the essential oil obtained from roots and aerial parts of I. cylindrica. Phytol, palmitic acid and p-vinylguaiacol did not show significant growth inhibitory activity against Lactuca sativa L. and Agrostis stolonifera L. Tabanone inhibited the growth of Lemna aequinoctialis Welw., L. sativa and Allium cepa L. The concentrations required for 50% growth inhibition of tabanone on L. aequinoctialis, L. sativa and A. cepa were 0.094, 6.5 and 3.6 mM, respectively. Tabanone also caused the electrolyte leakage of the cotyledon discs of Cucumis sativus L. and reduced photosynthetic electron transport of the discs. However, tabanone was not found in the soil under I. cylindrica [80].

Contribution of Allelopathy of I. cylindrica to Its Invasiveness
I. cylindrica shows high reproductive ability through seeds and rhizomes; its high growth rate and highly competitive ability with native plant species is described in the "Introduction" section [1,27,31,33,36,37]. Its phenotypic plasticity is also high, and it has adapted to a wide range of soil and climate conditions [7,43]. The species alters wildfire regimes and increases mortality of native plant species. None insects, fungi or other predators cause extensive damage to I. cylindrica populations [21]. These characteristics may contribute to the invasiveness of I. cylindrica and its naturalization. Many studies also suggest that its allelopathy may contribute to its invasiveness and naturalization [5,15,54,84].
The leachates, root exudates, residues and extracts of the plant parts of I. cylindrica exhibit allelopathic activity against the seed germination and growth of several plant species, including native plant species (Table 1). Several allelochemicals, such as fatty acids, terpenoids, simple phenolics, benzoic acid, phenolic acids, phenolic aldehydes, phenylpropanoids, flavonoids, quinone and alkaloids, were also isolated and identified in the leachates, root exudates, essential oil and extracts of I. cylindrica (Table 2; Figure 2). The derivatives of cinnamic acid and benzoic acid have been found in a wide range of plants and soils. Their inhibitory activity with respect to plant growth and germination is concentration-dependent. These compounds are often mentioned as putative allelochemicals, although their levels in soil and plants are differ significantly between publications. The derivatives of cinnamic acid and benzoic acid are synthesized by the shikimic acid pathway and serve as precursors for a wide variety of important compounds, playing crucial roles in plant fitness, including plant hormones and defense compounds [85]. Cinnamic acid and benzoic acid derivatives affect cell membrane permeability and reduce the potential of ion and nutrient uptake. They also affect stomatal functions and water balance and interfere with several enzyme activities involved in major physiological processes, such as respiration, protein synthesis, phytohormone synthesis and metabolism of some other secondary metabolites [86][87][88][89]. Therefore, cinnamic acid and benzoic acid derivatives found in I. cylindrica, such as benzoic acid, gentisic acid, gallic acid, p-hydroxybenzoic acid, vanillic acid, isoeugenol, cinnamic acid, p-coumaric acid, caffeic acid, ferulic acid and sinapinic acid, may affect some of those physiological processes of native plant species and decrease their germination, growth and fitness. Salicylic acid is a signaling molecule involved in plant defense systems against insect and fungal attacks, as well as other stress conditions [90,91]. Tabanone was reported to reduce photosynthetic electron transport [80]. Information on the mode of action of other compounds found in I. cylindrica is limited.
Recent pharmacological investigations showed that I. cylindrica contains secondary metabolites in many chemical classes, such as saponins, flavonoids, phenols and glycosides. in its rhizomes and other parts of the plants. Some of those compounds exhibited anti-inflammatory, antitumor, antibacterial, hematuria and diuretic activity in previous studies [92][93][94][95][96][97][98]. Although the allelopathic activity of most identified compounds has not yet been reported to date, a number of secondary metabolites in the invasive plants showed multiple effects, such as antiherbivore, antifungal and allelopathic activity [24,51,99]. Therefore, some of those compounds may exhibit growth inhibitory activity as allelopathic agents. It was reported that I. cylindrica may alter the microbial community in invaded soil and enhance the decomposition process of plant residues [54]. The rhizobium nodulation and mycorrhizal colonization of native plant species were significantly lower in I. cylindrica-infested plantations [59]. The leachates and exudates of I. cylindrica suppressed the mycorrhizal colonization of Aristida stricta Michex. var. beyrichiana and Pinus elliottii Engelm [66]. In addition, aqueous extracts of I. cylindrica shoots suppressed the rhizobium nodulation and arbuscular mycorrhizal colonization of Vigna radiata (L.) Wilczek and Phaseolus vulgaris L. [77]. These observations suggest that certain compounds of I. cylindrica may be involved in the alteration of the microbial community, including rhizobia and mycorrhizal fungi. Symbiosis with arbuscular mycorrhizal fungi is important for most territorial plants, and rhizobium nodulation is also important for leguminous plants. Arbuscular mycorrhizal fungi increase the ability of plants to absorb water and nutrients and enhance the defense function against several stress conditions and pathogen attacks [100][101][102]. Rhizobia establish root nodules of legumes, fix nitrogen and supply ammonium to host plants [103,104]. These observations suggest that I. cylindrica may be able to degrade the fungal and bacterial mutualisms of nearby plants. Reductions in rhizobium nodulation and mycorrhizal colonization weaken the ability of native plants to absorb water and nutrients, as well as their defense functions, which may result in growth inhibition of the native plants. It was also reported that other invasive plant species, such as Lantana camara L. and Fallopia japonica (Houtt.) Ronse Decraene, alter the microbial community, which is involved in the mycorrhizal colonization and the decomposition process of plant residues [105][106][107][108][109][110]. As described above, I. cylindrica may directly interrupt the regeneration process of native plant species by decreasing their germination and growth and indirectly via the suppression of mycorrhizal colonization and rhizobium nodulation of native plant species through its allelopathy. Therefore, the allelopathy of I. cylindrica may contribute to its enhanced competitive ability, as well as its invasiveness (Figure 3). Catechin (flavonoid) was once considered to contribute to the invasion of Centaurea stoebe L. from Europe into North America [49,50]. According to the novel weapon hypothesis, C. stoebe would release a certain amount of catechin into the rhizosphere soil, and the released catechin could suppress the regeneration process of indigenous plant species in North America through the inhibition of their germination and growth, contributing to the formation of C. stoebe monospecific stands [50,51]. However, the actual catechin levels in the rhizosphere soil were very low and could not induce significant inhibition of indigenous plant species [111]. The consequence suggests that the levels of allelochemicals in the rhizosphere soil and/or surrounding environments of invasive plants should be determined. Some allelochemicals were found in leachates, root exudate and growth medium of I. cylindrica [64,66,67]. However, it was also reported that some allelochemicals were absorbed onto soil particles. Some of those allelochemicals were not liberated with soil water and could not work as allelopathic agents [112][113][114].
Therefore, a discussion of the specific inhibitory activity of the identified allelochemicals and their concentrations in the rhizosphere soil water and/or surrounding environments is necessary to evaluate the contribution of these allelochemicals to the invasiveness of I. cylindrica.
in the rhizosphere soil were very low and could not induce significant inhibition of indigenous plant species [111]. The consequence suggests that the levels of allelochemicals in the rhizosphere soil and/or surrounding environments of invasive plants should be determined. Some allelochemicals were found in leachates, root exudate and growth medium of I. cylindrica [64,66,67]. However, it was also reported that some allelochemicals were absorbed onto soil particles. Some of those allelochemicals were not liberated with soil water and could not work as allelopathic agents [112][113][114]. Therefore, a discussion of the specific inhibitory activity of the identified allelochemicals and their concentrations in the rhizosphere soil water and/or surrounding environments is necessary to evaluate the contribution of these allelochemicals to the invasiveness of I. cylindrica.

Conclusions
I. cylindrica is highly invasive and has been naturalized in humid tropics, subtropics and warmer temperate zones of the world. Large monospecific stands of I. cylindrica are often observed in several countries. Its characteristics of life history, such as high reproduction and growth rates, competitive ability, phenotypic plasticity and defense ability against natural enemies may contribute to the invasiveness of the species. It was also shown that I. cylindrica possesses allelopathic properties (Table 1) and contains allelochemicals (Table 2, Figure 2), some of which were found in leachates, root exudates and growth medium of I. cylindrica, suggesting that certain allelochemicals may be released

Conclusions
I. cylindrica is highly invasive and has been naturalized in humid tropics, subtropics and warmer temperate zones of the world. Large monospecific stands of I. cylindrica are often observed in several countries. Its characteristics of life history, such as high reproduction and growth rates, competitive ability, phenotypic plasticity and defense ability against natural enemies may contribute to the invasiveness of the species. It was also shown that I. cylindrica possesses allelopathic properties (Table 1) and contains allelochemicals (Table 2, Figure 2), some of which were found in leachates, root exudates and growth medium of I. cylindrica, suggesting that certain allelochemicals may be released into the rhizosphere soil and/or surrounding environments. The leachates, exudates and extracts of I. cylindrica also altered the microbial community and suppressed the rhizobium nodulation and mycorrhizal colonization of native plant species, suggesting that certain compounds of I. cylindrica may be involved in the alteration of the microbial community, including rhizobia and mycorrhizal fungi. Mycorrhizal colonization increases the ability of plants to absorb water and nutrients and enhances the defense ability against several stress conditions and pathogen attacks. Rhizobia induce the root nodulation of legumes and supply nitrogen to the host plants. Therefore, the suppression of rhizobium nodulation and mycorrhizal colonization reduces the competitive ability and vigor of native plant species. Allelochemicals of the species may also suppress the regeneration process of native plant species through the inhibition of their germination and growth. Therefore, allelochemicals released from I. cylindrica may provide the species with a competitive advantage against native plant species, interrupting the regeneration process of native plants. The allelopathy of I. cylindrica may contribute to its invasiveness and naturalization as an invasive plant species.