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Article

Allelopathic Activity of the Invasive Plant Polygonum chinense Linn. and Its Allelopathic Substances

1
Department of Applied Biological Science, Faculty of Agriculture, Kagawa University, Miki 761-0795, Kagawa, Japan
2
The United Graduate School of Agricultural Sciences, Ehime University, Matsuyama 790-8566, Ehime, Japan
3
Graduate School of Engineering and Science, University of the Ryukyus, Nishihara 903-0213, Okinawa, Japan
4
Faculty of Education, University of the Ryukyus, Nishihara 903-0213, Okinawa, Japan
*
Author to whom correspondence should be addressed.
Plants 2023, 12(16), 2968; https://doi.org/10.3390/plants12162968
Submission received: 19 July 2023 / Revised: 11 August 2023 / Accepted: 15 August 2023 / Published: 17 August 2023
(This article belongs to the Special Issue Plant Allelopathy and Allelochemicals II)

Abstract

:
Polygonum chinense Linn., belonging to the Polygonaceae family, is distributed mostly in northern temperate climates. This species is a high-risk invasive plant and is thought to possess allelopathic potential. This study aimed to isolate and identify the allelopathic substances from P. chinense. Aqueous methanol extracts of P. chinense significantly inhibited the growth of alfalfa and Italian ryegrass seedlings in a species- and concentration-dependent manner. Activity-guided fractionation led to the isolation of two active compounds: dehydrovomifoliol and loliolide. A cress bioassay was used to determine the biological activity of dehydrovomifoliol, and cress, alfalfa, and Italian ryegrass were used to determine loliolide. Dehydrovomifoliol significantly suppressed the seedling growth of cress at the concentration of 1 mM, and the concentrations necessary for 50% growth inhibition (I50 values) of the roots and shoots were 1.2 and 2 mM, respectively. Loliolide significantly suppressed the shoot growth of cress, alfalfa, and Italian ryegrass at the concentration of 1 mM, and the concentrations necessary for I50 values of the shoots and roots were 0.15 to 2.33 and 0.33 to 2.23 mM, respectively. The findings of our study suggest the extracts of P. chinense might have growth-inhibitory potential and that dehydrovomifoliol and loliolide might contribute as allelopathic agents.

Graphical Abstract

1. Introduction

Polygonum chinense Linn., a rhizomatous herbaceous perennial from the Polygonaceae family, is commonly known as Chinese knotweed or smartweed (Figure 1). Polygonum chinense is widespread across Vietnam, Bhutan, Taiwan, China, Indian Subcontinent, Japan, South Korea, North Korea, Indonesia, Malaysia, Nepal, Papua New Guinea, the Philippines, Sri Lanka, Myanmar (Burma), and Thailand [1]. Polygonum chinense can be found in disturbed areas such as home gardens, abandoned gardens, and roadsides [1,2]. In natural environments, it can be found in forests and on riverbanks, and grows from sea level to 3000 m [3], especially in areas of regrowth and natural clearings [1,4,5], where it may disrupt forest regeneration [5]. This species is used in herbal remedies, such as for the treatment of sore throat, dysentery, and enteritis in Malaysia and Vietnam [6], and for the treatment of skin diseases and inflammation in traditional medicine in Myanmar [7], and in India, Japan, China, and Southeast Asian countries [8,9,10]. On the other hand, this species is a high-risk invasive species and tolerates a wide range of environmental conditions in Asia and coastal areas of New South Wales and Queensland in Australia [11]. The P. chinense grows up to approximately 1 to 1.5 m and has prominent nodes. Their stems and branches are spineless, reddish-purple, and lack hair arranged with alternate leaves and ovate to oblong shape. The size of the flowers is small, and their colors are white or light reddish and arranged in capitate, inflorescence axillary. Fruits are berries, shaped of globose with black and small seeds. The plant grows rapidly, forming thick canopies that can smother native plants [2], and is perceived as an environmental weed that suppresses other plant species with its dense mats [5,12,13].
Polygonum chinense is one of the undesirable weeds that continually evolve, survive, thrive, and reproduce weeds in tea plantations and can infest severely in mature tea [14,15], especially in southern India [16] where it blocks the drainage systems and covers the tea bushes. It could have the potential to affect nursery operations, orchards, and forestry [17], and it is listed as an “agricultural weed” in Thailand and Taiwan [12]. Allelochemicals produced by invasive weed species disrupt the fundamental physiological processes of crops, restricting their growth and development. Consequently, weeds compete with crops for environmental resources [18]. Compared with other plant species, weeds have more genetic variety and phenotypic plasticity [19,20,21].
Traditional explanations for biological invasions rely on several premises, including enemy release hypotheses, disturbance, biotic resistance, and so on [22]. Invasive plants may have particularly potent allelopathic effects, according to the novel weapons hypothesis [21,23], because introduced plants did not coevolve with the invader and are therefore more vulnerable to its allelopathic compounds than native plants [20]. Allelopathic effects play a role in the success of various plant invaders, such as spotted knapweed [24,25], garlic mustard [26,27], Canada golden rod [28,29], sticky snakeroot [30], bitter bush [31], and Japanese knotweed [23,32]. By releasing chemical compounds into the environment, such invasive exotic species displace local plants, making it easier for the invasive species to become established [24,33,34]. In growth assays, aqueous extracts of knotweed species inhibit other plant species [35,36], which suggested that invasive knotweeds may produce allelochemicals that act as novel weapons and facilitate monodominance. Polygonum chinense is of particular interest experimentally because it has the ability not only to invade forests, habitats that are typically considered to be relatively suppressed by other plant species with their dense mats, but also to be used as herbal remedies. In our previous study, aqueous methanol extracts of P. chinense showed growth-inhibitory activity, and two inhibitory compounds were isolated [37]. Notably, there were other active fractions that may contain other inhibitory substances. Accordingly, this experiment was conducted to evaluate the growth-inhibitory activity of P. chinense extracts on another two test plants, to isolate the plant growth-inhibitory substances, and to assess the activity of the growth-inhibitory substances.

2. Results

2.1. Allelopathic Activity of the Polygonum chinense Plants

The extracts of P. chinense above plant parts inhibited the shoot and root growth of both the test plants (alfalfa and Italian ryegrass) at the lowest concentration of 0.001 g dry weight (DW) equivalent extract/mL (Figure 2). The concentration of 0.01 g DW equivalent extract/mL of P. chinense suppressed the shoot growth of alfalfa and Italian ryegrass to 36.18 and 23.47% of the control, respectively, and suppressed the root growth to 41.13 and 49.19%, respectively. The extract obtained from 0.3 g of P. chinense completely suppressed the shoot and root growth of alfalfa and Italian ryegrass. The concentrations needed to inhibit the growth of the alfalfa and Italian ryegrass shoots by 50% (I50 values) were 0.0035 and 0.043 g DW equivalent extract/mL, respectively, and 0.0049 and 0.0052 for the root growth (Table 1), respectively.

2.2. Isolation and Purification of the Allelopathic Substances

A schematic diagram of the isolation procedure of the substances is shown in Figure 3. The ethyl acetate and aqueous fractions of the P. chinense extracts retarded the seedling growth of the cress in a dose-dependent manner (Figure 4). At the concentration of 0.3 g DW equivalent extract/mL, both fractions completely inhibited the shoot growth of the cress and inhibited the root growth to less than 2% of the control. The ethyl acetate fraction was subjected to further purification steps using a column of silica gel, resulting in fraction 6 (F6) showing the most inhibitory activity followed by fractions F7, F5, F4, F9, and so on (Figure 5). Therefore, the most active fraction of F6 and the second active fraction of F7 were chosen for continuing the purification process and purified through a Sephadex LH-20 column and reverse-phase C18 cartridges, and finally, two active compounds were isolated by using reverse-phase HPLC, which was characterized by analyzing the spectral data.

2.3. Characterization and Biological Activity of Compound 1

The molecular formula of compound 1, a colorless oil, was found to be C13H17O3 as determined by HRESIMS (high-resolution electrospray ionization mass spectroscopy) m/z 245.1147 [M + Na]+ (calcd for C13H18O3Na 245.1148). The 1H NMR (proton nuclear magnetic resonance) spectrum of compound 1 as measured in CD3OD showed four methyl proton signals at δH 2.31 (3H, s), 1.90 (3H, s), 1.06 (3H, s), and 1.02 (3H, s); three olefinic proton signals at δH 6.99 (1H, d, J = 15.8), 6.44 (1H, d, J = 15.8), and 5.94 (1H, s); and two methylene proton signals at δH 2.60 (1H, d, J = 17.2) and 2.28 (1H, d, J = 17.2). The 1H NMR spectrum of compound 1 was in agreement with the reported data of dehydrovomifoliol (Figure 6) [38].
The biological activity of dehydrovomifoliol against cress was assayed. The results of the assay showed that the seedling growth of cress was significantly retarded at the concentration of 1 mM (Figure 7). At the concentration of 3 mM, dehydrovomifoliol suppressed the growth of seedlings by more than 50% of the control whilst at the concentration of 10 mM by more than 75% of the control. The I50 values for dehydrovomifoliol against the cress seedling roots and shoots were 1.2 and 2 mM (Table 2), respectively.

2.4. Characterization and Biological Activity of Compound 2

Compound 2 was an amorphous powder; [α]D24 = −82.8 (c 0.54, MeOH). Its molecular formula was found to be C11H16O3 as determined by HRESIMS m/z 197.1171 [M + H]+ (calcd for C11H17O3, 197.1172). The 1H NMR spectrum of compound 2 as measured in CD3OD showed three methyl proton signals at δH 1.76 (3H, s), 1.47 (3H, s), and 1.28 (3H, s); one olefinic proton signal at δH 5.75 (1H, s); one methine proton signal at δH 4.22 (1H, m); and four methylene proton signals at δH 2.42 (1H, dt, J = 13.8, 2.7), 1.99 (1H, dt, J = 14.4, 2.6), 1.75 (1H, dd, J = 13.8, 4.0), and 1.53 (1H, dd, J = 14.4, 3.7). The 1H NMR spectrum of compound 2 was in agreement with the reported data of loliolide (Figure 8) [39].
The biological activity of loliolide was evaluated against cress, alfalfa, and Italian ryegrass. The results from the bioassays showed that the cress seedlings were significantly suppressed at the concentration of 0.03 mM, and the alfalfa and Italian ryegrass seedlings were significantly suppressed at the concentration of 1 mM (Figure 9). The concentration of 10 mM completely suppressed the shoot growth of cress and that of the alfalfa and Italian ryegrass plants to less than 15% of control, whilst the root growth of the three test plants was suppressed to less than 15% of control. The I50 values for loliolide against the shoots of the test seedlings were in the range of 0.15 to 2.33 mM and for the roots were in the range of 0.33 to 2.23 mM (Table 3).

3. Discussion

The above plant parts extracts of Polygonum chinense (Chinese knotweed) significantly inhibited the growth of alfalfa and Italian ryegrass (Figure 2). Our previous experiment revealed that P. chinense plant extracts inhibited four test plants (cress, lettuce, timothy, and barnyard grass) [37]. The inhibitory effects of the plant extracts against the test plants increased with increasing extract concentration. Allelopathic substances, which are released by alien invasive plants, affect the germination of seeds and the development of native species [40,41]. The I50 values show that the inhibition by the plant extracts differed depending on the test plant species (Table 1). Such species-specific and dose-dependent inhibition has also been documented in other studies [42,43,44]. The findings are consistent with the earlier studies reporting that the inhibitory effect depended on the concentration of extracts, and the sensitivity to the extracts relied on the biochemical and physiological characteristics of each plant species [45,46]. Differences in the biochemical and physiological nature of test plants may be responsible for the inhibitory effects of the extracts [47]. Isolating and identifying secondary metabolites from natural sources (plants) is crucial for the development of ecologically friendly natural herbicides. In our previous experiment, two active compounds, (-)-3-hydroxy-β-ionone and (-)-3-hydroxy-7,8-dihydro-β-ionone, were isolated and identified from P. chinense plant extracts, and both identified compounds significantly retarded the seedling growth of cress [37]. In the present study on the P. chinense above plant parts extracts, two other active compounds were purified and characterized as dehydrovomifoliol (Figure 6) and loliolide (Figure 8) using several chromatographic methods (Figure 3).
Both compounds are reported as nor isoprenoids, and their antimicrobial, antiproliferative, anti-algal, antioxidant, and cytotoxic properties have been explored [48,49]. There are several different plant species that contain dehydrovomifoliol: Phaseolus vulgaris L. [50], Helianthus annuus L. cv. Peredovick [51], Beta vulgaris var. cicla [52], Malva silvestris [53], Cucumis sativa [38], Arctium lappa L. [54], Raphanus sativus L. [55], and Dregea volubilis (L.f.) Benth. ex. Hook. f. [43], and it has also been synthesized from C9-hydroxy ketone [56]. Ren et al. [57] reported that dehydrovomifoliol has cytotoxic effects against human cancer cells. Hodges and Porte (1964) reported firstly the loliolide compound from Lolium perenne L. and its diverse biological activities [58,59,60]. Since then, it has been found in different plant and animal species, in both land and sea ecosystems [61], such as Bunias orientalis L. [62], Centrostachys aquatica (R.Br.) Moq. [63], Digitaria sanguinalis (L.) Scop. [64], Marsilea crenata C. Presl [65], and Albizia richardiana (Voigt.) King and Prain [66], and it has also been obtained by synthesizing C11-aldehyde [56]. However, the isolation of dehydrovomifoliol and loliolide from Polygonum chinense has not yet been documented in the literature.
The results of our study showed that dehydrovomifoliol inhibited the growth of cress (Figure 7), and loliolide inhibited the growth of cress, alfalfa, and Italian ryegrass (Figure 9). The level of inhibition differed depending on the extract concentration, the species of the test plants, and the chemical structures of the compounds. Differences in allelopathic activity may be led by variations in the chemical structures of substances [67]. Numerous invading plant species have been found to be allelopathic, and their phytotoxic compounds have adverse effects on other plant species [68,69,70]. According to Dayan et al. [71], the varying levels of bio-effectiveness among the compounds may be due to the distinct mode of action that different compound structures have on target plants. The I50 values of loliolide (Table 3) showed the inhibitory effect differed with plant species. Dehydrovomifoliol is a C13-nor isoprenoid with two oxo groups at C-3 and C-9 and a hydroxyl group in the benzene ring. Loliolide, on the other hand, is a C11-nor isoprenoid structured in a benzene ring with a hydroxyl group at the C-3 position and one oxo group at the C-8 position (Figure 8). The I50 values of the two compounds show the cress seedlings were more sensitive to loliolide than dehydrovomifoliol. These results support the hypothesis of Kobayashi et al. [72] that the phytotoxic potential of loliolide may be due to the hydroxyl group at the C-3 position. The chemical structure, including the number and position of different functional groups replaced in the benzene ring, controls the toxicity of phytochemicals [73,74]. The findings in the present study designate that dehydrovomifoliol and loliolide have growth-inhibitory activity and may contribute to the allelopathic effect of P. chinense. As a result, P. chinense could be used as a soil additive resource or soil enhancement to manage weeds in an environmentally acceptable manner. Its plant residues may also be discharged into the soil and behave as allelopathic chemicals.

4. Materials and Methods

4.1. Extraction and Plant Material

Samples of Polygonum chinense were collected in different areas of Mandalay Region, Myanmar from July to August 2020 (Figure 1). After removing dust and contamination, all the samples were air-dried and ground. Ground dried powder (50 g) of the above plant parts of P. chinense was extracted using 300 mL of a mixture of distilled water and methanol (MeOH) in a ratio of 30:70 (v/v) for a couple of days. The crude extracts were filtrated through No. 2 filter paper (Toyo Roshi Kaisha Ltd., Tokyo, Japan), and the residues were re-extracted using 300 mL of MeOH for a day and filtrated again. Both filtrates were combined in one flask and evaporated until dry in a 40 °C vacuum using a rotary evaporator to produce the concentrated crude extract.

4.2. Growth-Inhibitory Assay

Medicago sativa L. (alfalfa) and Lolium multiflorum Lam. (Italian ryegrass) were selected to determine growth-inhibitory activity. The concentrated extract of P. chinense was diluted in 100 mL MeOH. Six different concentrations (0.001, 0.003, 0.01, 0.03, 0.1, and 0.3 g dry weight (DW) equivalent extract/mL) were used to evaluate the growth-inhibitory assay of the extracts on the test plants, and the exact extract amount was put on filter papers in each 2.8 cm Petri dishes. After the extract concentration was dried, the aqueous solution of 0.6 mL of 0.05% (v/v) of Tween 20 (polyoxyethylene sorbitan monolaurate; Nacalai Tesque, Inc., Kyoto, Japan) was put into the Petri dishes to moisten the filter paper, and then 10 dicot seeds of alfalfa and 10 monocot seeds of sprouted Italian ryegrass were placed in the Petri dishes. Only Tween 20 aqueous solutions were used for the control treatment. After incubation for a couple of days in darkness, seedling length was measured. The shoot and root growth of the test plants were measured by using a ruler. The inhibition was calculated by comparing the treatments of the extracts with the control of each test plant. To compute the inhibition % of seedling growth, the following formula was used.
( % ) s e e d l i n g   g r o w t h = 1 l e n g t h   o f   t r e a t e d   s e e d l i n g s l e n g t h   o f   c o n t r o l   s e e d l i n g s × 100

4.3. Isolation and Purification of the Growth-Inhibitory Substances

Polygonum chinense plant powder (2.1 kg) was extracted as described in Section 4.1 using 10 L of the exact ratio of distilled water and MeOH (ratio 30:70, v/v) and 10 L of MeOH. A rotary evaporator was then used to condense the extract at 40 °C to produce aqueous residues. A 1 M phosphate buffer solution was then used to bring the concentrated residues to pH 7.0. The equal volume of ethyl acetate was partitioned five times (150 mL each time) to obtain an aqueous (distilled water) fraction and an ethyl acetate fraction. The effects of the distilled water fraction and the ethyl acetate (EtOAc) fraction on growth suppression were evaluated using a cress assay. After being treated overnight with anhydrous sodium sulfate (Na2SO4 used to remove water), the ethyl acetate fraction was filtrated and subjected to the next purification procedures, and this fraction was then evaporated until completely dry.
The EtOAc fraction continued to be separated by a silica gel column (60 g of silica gel, spherical, 70–230 mesh: Nacalai Tesque, Kyoto, Japan.) eluted stepwise with the ratio of ethyl acetate in n-hexane 20:80 to 80:20 (v/v, 150 mL per step), 150 mL of ethyl acetate, and 300 mL of methanol. A cress assay was used to assess the biological effect of these nine fractions. The biological activity obtained from the separation of the silica gel column showed that there were two active fractions eluted with 30:70 and 20:80 EtOAc in n-hexane (v/v). The fraction eluted by 70% EtOAc in n-hexane was first conducted to isolate the active substances. The residues were evaporated to dry and then separated using a column of Sephadex LH-20 (80 g; Sigma-Aldrich, Burlington, VT, USA). Five different concentrations of aqueous methanol (20, 40, 60, 80%, v/v, 150 mL each step, and 300 mL of methanol), were loaded onto the Sephadex column. These fractions were evaporated until dry, and a growth assay of cress was carried out to determine how these fractions affected the biological processes. An inhibitory active fraction was eluted by 40% of aqueous methanol (F2). The active fraction was again evaporated until dry and diluted with 20% (v/v) aqueous methanol and loaded onto a reverse-phase of C18 Sep-Pak cartridge (YMC Co., Ltd., Kyoto, Japan). Seven different concentrations of aqueous methanol (20 to 70%, v/v, 15 mL each step, and 30 mL of methanol) were loaded on the C18 Sep-Pak cartridge. The most active fraction was eluted in fraction 3 (40% aqueous methanol).
Fraction 3 was then isolated by running reverse-phase of high-performance liquid chromatography (HPLC; I.D. ODS, 500 × 10 mm, Shimadzu Corporation, Kyoto, Japan) eluted with 40% (v/v) aqueous methanol at a flow rate of 1.5 mL/min. The active peak was detected at a wavelength of 220 nm in a 40 °C oven at a retention time of 95–99 min. The active peak was purified once again by running HPLC (S-5 µm, 4.6 mm × 250 mm I.D., Inertsil® ODS-3; GL Science Inc., Tokyo, Japan) eluted with 40% (v/v) aqueous methanol at a flow rate of 0.8 mL/min. Compound 1 was detected in a retention time of 16–17 min and an oven temperature of 40 °C at 220 nm.
Another compound was isolated from the silica gel column (fraction 7), the Sephadex LH-20 column (fraction 2), the C18 Sep-Pak cartridge column (fraction 2), and running HPLC (500 × 10 mm I.D. ODS AQ-325; Shimadzu Corporation, Kyoto, Japan) eluted 50% aqueous methanol at a flow rate of 1.5 mL/min, and detected in a retention time of 84–89 min, at an oven temperature of 40 °C at 220 nm. Compound 2 was then purified once again at a flow rate of 0.8 mL/min with 35% aqueous methanol by running reverse-phase HPLC (S-5 µm, 4.6 × 250 mm I.D., Inertsil ® ODS-3; GL Science Inc.), and the pure peak was obtained at the retention time of 38–41 min. Finally, spectral analysis was used to characterize the chemical structures of these two compounds. A schematic diagram of the isolation procedure of the two substances is presented in Figure 3.

4.4. Bioassay of the Identified Compounds

The two compounds were dissolved in 3 mL of methanol separately to obtain solutions at five concentrations of 0.03, 0.1, 0.3, 1, 3, and 10 mM, which were prepared and added to Petri dishes (2.8 cm diameter) lined with filter paper. Cress seeds were used to test the inhibitory effect of compound 1, and sprouted seeds of Italian ryegrass (monocot) and seeds of alfalfa and cress (dicots) were used to test the inhibitory effect of compound 2 as described in Section 4.2. Each treatment was conducted with three replicates (n = 30).

4.5. Spectral Data

A JASCO P-1010 polarimeter was used to measure the optical rotation. All NMR spectroscopic data were recorded on a Bruker AVANCE III 500 MHz NMR spectrometer. Chemical shifts were reported relative to the residual solvent signal (CD3OD: δH 3.31). HRESIMS was performed using a Thermo Scientific Orbitrap Exploris 240 mass spectrometer.

4.6. Statistical Analysis

The assay experiments were arranged in a completely randomized block design (10 seeds for each treatment) with three replicates. The results are shown as mean ± SE (standard error). The ANOVA and Tukey’s honestly significant difference (HSD) test for multiple comparisons were performed using Version 16.0 of the Statistical Package for the Social Sciences, SPSS, IBM, Armonk, NY, USA, with a significance level of 0.05. The I50 values were analyzed using GraphPad Prism Version 6.0 software package, San Diego, CA, USA.

5. Conclusions

The aqueous methanol extracts of the Polygonum chinense plant showed allelopathic activity. The two active allelopathic substances were isolated from the silica gel column of two different fractions and characterized as dehydrovomifoliol and loliolide. These two compounds showed allelopathic effects against each test plant. The findings of our study showed that these two compounds possess allelopathic potential and may contribute through the decomposition of plant residues and possibly act as allelopathic agents. However, more research is needed to examine the mechanisms underlying the allelopathy of P. chinense, the role of allelochemicals of different functional groups, and the long-term effects of allelopathy in soil residues.

Author Contributions

Conceptualization, T.L.L. and H.K.-N.; methodology, T.L.L., S.T., T.T. and H.K.-N.; software, T.L.L.; validation, S.T., T.T. and H.K.-N.; formal analysis, T.L.L.; investigation, T.L.L.; data curation, H.K.-N.; writing (original draft preparation), T.L.L.; writing (review and editing), H.K.-N.; visualization, T.L.L.; supervision, H.K.-N. All authors have read and agreed to the published version of the manuscript.

Funding

This research received funding from a MEXT scholarship (Grant Number MEXT-203629) from the government of Japan.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

We acknowledge Dennis Murphy, the United Graduate School of Agricultural Sciences, Ehime University, Japan, for editing the English of this manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. U.S. Forest Service. Pacific Island Ecosystems at Risk (PIER): Plant threats to Pacific Ecosystems. United States Forest Service, United States Department of Agriculture. 2010. Available online: http://www.hear.org/pier/index.html (accessed on 2 June 2023).
  2. Galloway, D.J.; Lepper, V.E. Persicaria chinensis—A New Alien Asian Invader? In Proceedings of the 17th Australasian Weeds Conference, Christchurch, New Zealand, 26–30 September 2010; pp. 174–175. Available online: http://www.caws.org.au/awc/2010/awc201011741.pdf (accessed on 2 June 2023).
  3. eFloras. Flora of North America; Missouri Botanical Garden: St. Louis, MO, USA; Harvard University Herbaria: Cambridge, MA, USA, 2003; Available online: http://www.efloras.org/flora_page.aspx?flora_id=1 (accessed on 7 April 2023).
  4. eFloras. Flora of China; Missouri Botanical Garden: St. Louis, MO, USA; Harvard University Herbaria: Cambridge, MA, USA, 2003; Available online: http://www.efloras.org/flora_page.aspx?flora_id=2 (accessed on 7 April 2023).
  5. Goodland, T.; Healey, J.R. The Invasion of Jamaican montane Rainforests by the Australian Tree Pittosporum undulatum in the Blue Mountains of Jamaica; School of Agricultural and Forest Sciences, University of Wales: Bangor, UK, 1996; 55p. [Google Scholar]
  6. Tanaka, Y.; Van-Ke, N. Edible Wild Plants of Vietnam: The Bountiful Garden; Orchid Press: Bangkok, Thailand, 2007; p. 121. ISBN 978-9-74524-089-6. [Google Scholar]
  7. Aung, A.T.; Ohn, T.M. Morphological characters, histological characters and nutritional values of Polygonum chinense L. J. Myanmar Acad. Arts Sci. 2018, 16, 4. [Google Scholar]
  8. Xiao, H.; Tsang, S.; Qin, H.; Choi, F.F.K.; Yang, Z.; Han, Q.; Chen, H.; Xu, H.; Shen, H.; Lu, A.; et al. A bioactivity-guided study on the anti-diarrheal activity of Polygonum chinense Linn. J. Ethnopharmacol. 2013, 149, 499–505. [Google Scholar] [CrossRef] [PubMed]
  9. Tran, T.T.; Kim, M.; Jang, Y.; Lee, H.W.; Nguyen, H.T.; Nguyen, T.N.; Park, H.W.; Le Dang, Q.; Kim, J.C. Characterization and mechanisms of anti-influenza virus metabolites isolated from the Vietnamese medicinal plant Polygonum chinense. BMC Complement. Altern. Med. 2017, 17, 162. [Google Scholar] [CrossRef] [PubMed]
  10. Zeng, J.; Chen, D.; Chunli, L.; Qin, K.; Zhou, Q.; Pu, N.; Song, S.; Wang, X. Antimicrobial and anti-biofilm activity of Polygonum chinense L. aqueous extract against Staphylococcus aureus. Sci. Rep. 2022, 12, 21988. [Google Scholar] [CrossRef]
  11. PPQ. Weed Risk Assessment for Persicaria chinensis (L.) H. Gross (Polygonaceae)—Chinese Knotweed; United States Department of Agriculture, Animal and Plant Health Inspection Service, Plant Protection and Quarantine (PPQ): Raleigh, NC, USA, 2017; p. 25. [Google Scholar]
  12. Randall, R.P. A Global Compendium of Weeds. Hawaiian Ecosystems at Risk and Department of Agriculture of Western Australia. 2007. Available online: http://www.hear.org/gcw/ (accessed on 16 September 2022).
  13. Waugh, J. Trade Related Pathways to the Introduction of Terrestrial Invasive Species in the Insular Caribbean (Report to International Programs, US Forest Service) (Draft); International Union for Conservation of Nature: Gland, Switzerland, 2008; p. 37. [Google Scholar]
  14. Rao, V.S.; Rahman, F.; Sharma, S.N.; Singh, H.S. Control of persistent weeds of tea. In Proceedings of the 28th Tocklai Biennial Conference, Jorhat, India, 24–26 November 1977; pp. 61–64. [Google Scholar]
  15. Chakravartee, J. Weed control in tea. Two Bud 1994, 41, 2–11. [Google Scholar]
  16. Haridas, P.; Sharma, V.S. Some common weeds of South Indian tea fields. 14. Polygonum chinense L. and Calceolaria mexicana Benth. Plant. Chron. 1974, 69, 379–380. [Google Scholar]
  17. Biosecurity New Zealand. Chinese Knotweed, Persicaria chinensis. New Zealand Government, Biosecurity New Zealand. Available online: https://www.biosecurity.govt.nz/pests/chinese-knotweed (accessed on 14 October 2011).
  18. Farooq, N.; Abbas, T.; Tanveer, A.; Jabran, K. Allelopathy for weed management. In Co-Evolution of Secondary Metabolites; Merillon, J.M., Ramawat, K., Eds.; Springer International Publishing: Cham, Switzerland, 2020; pp. 1–16. [Google Scholar]
  19. Singh, V.V.; Singh, S.K.; Pratap, T. Tank mix herbicide combination effect on weed and yield of wheat in North-Eastern plain zone. Pharma Innov. J. 2020, 11, 1359–1362. [Google Scholar]
  20. Bufford, J.L.; Hulme, P.E. Increased adaptive phenotypic plasticity in the introduced range in alien weeds under drought and flooding. Biol. Invasions 2021, 23, 2675–2688. [Google Scholar] [CrossRef]
  21. Callaway, R.M.; Ridenour, W.M. Novel weapons: Invasive success and the evolution of increased competitive ability. Front. Ecol. Environ. 2004, 2, 436–443. [Google Scholar] [CrossRef]
  22. Ma, H.; Chen, Y.; Chen, J.; Ji, J.; He, H. Identification and comparison of allelopathic effects from leaf and flower volatiles of the invasive plants’ Mikania micrantha. Chemoecology 2021, 31, 355–365. [Google Scholar] [CrossRef]
  23. Kato-Noguchi, H. Allelopathy of knotweeds as invasive plants. Plants 2022, 11, 3. [Google Scholar] [CrossRef] [PubMed]
  24. Ridenour, W.M.; Callaway, R.M. The relative importance of allelopathy in interference: The effects of an invasive weed on a native bunchgrass. Oecologia 2001, 126, 444–450. [Google Scholar] [CrossRef] [PubMed]
  25. Callaway, R.M.; Aschehoug, E.T. Invasive plants versus their new and old neighbors: A mechanism for exotic invasion. Science 2000, 290, 521–523. [Google Scholar] [CrossRef] [PubMed]
  26. Stinson, K.A.; Campbell, S.A.; Powell, J.R.; Wolfe, B.E.; Callaway, R.M.; Thelen, G.C.; Hallett, S.G.; Prati, D.; Klironomos, J.N. Invasive plants suppress the growth of native tree seedlings by disrupting belowground mutualisms. PLoS Biol. 2006, 4, e140. [Google Scholar] [CrossRef] [PubMed]
  27. Callaway, R.M.; Cipollini, D.; Barto, K.; Thelen, G.C.; Hallett, S.G.; Prati, D.; Stinson, K.; Klironomos, J. Novel weapons: Invasive plant suppresses fungal mutualists in America but not in its native Europe. Ecology 2008, 89, 1043–1055. [Google Scholar] [CrossRef]
  28. Yang, R.Y.; Mei, L.X.; Tang, J.J.; Chen, X. Allelopathic effects of invasive Solidago canadensis L. on germination and growth of native Chinese plant species. Allelopath. J. 2007, 19, 241–247. [Google Scholar]
  29. Abhilasha, D.; Quintana, N.; Vivanco, J.; Joshi, J. Do allelopathic compounds in invasive Solidago canadensis restrain the native European flora? J. Ecol. 2008, 96, 993–1001. [Google Scholar] [CrossRef]
  30. Li, Y.-P.; Feng, Y.-L.; Kang, Z.-L.; Zheng, Y.-L.; Zhang, J.-L.; Chen, Y.-J. Changes in soil microbial communities due to biological invasions can reduce allelopathic effects. J. Appl. Ecol. 2017, 54, 1281–1290. [Google Scholar] [CrossRef]
  31. Zheng, Y.L.; Feng, Y.L.; Zhang, L.K.; Callaway, R.M.; Valiente-Banuet, A.; Luo, D.Q.; Liao, Z.Y.; Lei, Y.B.; Barclay, G.F.; Silva-Pereyra, C. Integrating novel chemical weapons and evolutionarily increased competitive ability in success of a tropical invader. New Phytol. 2015, 205, 1350–1359. [Google Scholar] [CrossRef]
  32. Bourchier, R.S.; Van Hezewijk, B.H. Distribution and potential spread of Japanese knotweed (Polygonum cuspidatum) in Canada relative to climatic thresholds. Invasive Plant Sci. Manag. 2010, 3, 32–39. [Google Scholar] [CrossRef]
  33. Bais, H.P.; Vepachedu, R.; Gilroy, S.; Callaway, R.M.; Vivanco, J.M. Allelopathy and exotic plant invasion: From molecules and genes to species interactions. Science 2003, 301, 1377–1379. [Google Scholar] [CrossRef] [PubMed]
  34. Wan, F.; Liu, W.; Guo, J.; Qiang, S.; Li, B.; Wang, J.; Yang, G.; Niu, H.; Gui, F.; Huang, W.; et al. Invasive mechanism and control strategy of Ageratina adenophora (Sprengel). Sci. China Life Sci. 2010, 53, 1291–1298. [Google Scholar] [CrossRef]
  35. Inoue, M.; Nishimura, H.; Li, H.H.; Mizutani, J. Allelochemicals from Polygonum sachalinense Fr. Schm. (Polygonaceae). J. Chem. Ecol. 1992, 18, 1833–1840. [Google Scholar] [CrossRef] [PubMed]
  36. Murrell, C.; Gerber, E.; Krebs, C.; Parepa, M.; Schaffner, U.; Bossdorf, O. Invasive knotweed affects native plants through allelopathy. Am. J. Bot. 2011, 98, 38–43. [Google Scholar] [CrossRef] [PubMed]
  37. Lun, T.L.; Iwasaki, A.; Suenaga, K.; Kato-Noguchi, H. Isolation and identification of plant-growth inhibitory constituents from Polygonum chinense Linn and evaluation of their bioherbicidal potential. Plants 2023, 12, 1577. [Google Scholar] [CrossRef] [PubMed]
  38. Hisahiro, K.; Masaki, B.; Toru, O. Two new megastigmanes from the leaves of Cucumis sativus. Chem. Pharm. Bull. 2007, 55, 133–136. [Google Scholar]
  39. Mi-Ran, K.; Seung-Kyu, L.; Chang-Soo, K.; Kyung-Soon, K.; Dong-Cheul, M. Phytochemical constituents of Carpesium macrocephalum FR- et SAV-. Arch. Pharm. Res. 2004, 27, 1029–1033. [Google Scholar]
  40. Tokarska-Guzik, B.; Dajdok, Z.; Zając, M.; Zając, A.; Urbisz, A.; Danielewicz, W.; Hołdyński, C. Rośliny Obcegopochodzenia w Polsce ze Szczególnym Uwzględnieniem Gatunków Inwazyjnych (Plants of Foreign Origin in Poland, with Particular Emphasis on Invasive Species); Generalna Dyrekcja Ochrony Środowiska: Warszawa, Poland, 2012; p. 196. [Google Scholar]
  41. Yuan, Y.G.; Wang, B.; Zhang, S.S.; Tang, J.J.; Tu, C.; Hu, S.J.; Chen, X. Enhanced allelopathy and competitive ability of invasive plant Solidago canadensis in its introduced range. J. Plant Ecol. 2013, 6, 253–263. [Google Scholar] [CrossRef]
  42. Suzuki, M.; Iwasaki, A.; Suenaga, K.; Kato-Noguchi, H. Phytotoxic property of the invasive plant Tithonia diversifolia and a phytotoxic substance. Acta Biol. Hung. 2017, 68, 187–195. [Google Scholar] [CrossRef]
  43. Kyaw, E.H.; Iwasaki, A.; Suenaga, K.; Kato-Noguchi, H. Assessment of the phytotoxic potential of Dregea volubilis (L.f.) Benth. ex Hook. f. and identification of its phytotoxic substances for weed control. Agriculture 2022, 12, 1826. [Google Scholar] [CrossRef]
  44. Moh, S.M.; Kurisawa, N.; Suenaga, K.; Kato-Noguchi, H. Allelopathic potential of Marsdenia tenacissima (Roxb.) Moon against four test plants and the biological activity of its allelopathic novel compound, 8-dehydroxy-11β-O-acetyl-12β-O-tigloyl-17β-marsdenin. Plants 2023, 12, 1663. [Google Scholar] [CrossRef] [PubMed]
  45. Moosavi, A.; Afshari, R.T.; Asadi, A.; Gharineh, M.H. Allelopathic effects of aqueous extract of leaf stem and root of Sorghum bicolor on seed germination and seedling growth of Vigna radiata L. Not. Sci. Biol. 2011, 3, 114–118. [Google Scholar] [CrossRef]
  46. Mousavi, S.H.; Alami-Saeid, K.H.; Moshatati, A. Effect of leaf, stem and root extract of alfalfa (Melilotus indicus) on seed germination and seedling growth of wheat (Triticum aestivum). Int. J. Agric. Sci. 2013, 5, 44–49. [Google Scholar]
  47. Sodaeizadeh, H.; Rafieiolhossaini, M.; Havlík, J.; van Damme, P. Allelopathic Activity of Different Plant Parts of Peganum harmala L. and Identification of Their Growth Inhibitors Substances. Plant Growth Regul. 2009, 59, 227–236. [Google Scholar] [CrossRef]
  48. Ragasa, C.Y.; De Luna, R.D.; Hofilena, J.G. Antimicrobial terpenoids from Pterocarpus indicus. Nat. Prod. Res. 2005, 19, 305–309. [Google Scholar] [CrossRef] [PubMed]
  49. Lu, H.; Xie, H.; Gong, Y.; Wang, Q.; Yang, Y. Secondary metabolites from the seaweed Gracilaria lemaneiformis and their allelopathic effects on Skeletonema costatum. Biochem. Syst. Ecol. 2011, 39, 397–400. [Google Scholar] [CrossRef]
  50. Takasugi, M.; Anetai, M.; Katsui, N.; Masamune, T. The occurrence of vomifoliol, dehydrovomifoliol and dihydrophaseic acid in the roots of “kidney bean” (Phaseolus vulgaris L.). Chem. Lett. 1973, 2, 245–248. [Google Scholar] [CrossRef]
  51. Macías, F.A.; Oliva, R.M.; Varela, R.M.; Torres, A.; Molinillo, J.M. Allelochemicals from sunflower leaves cv. Peredovick. Phytochem. 1999, 52, 613–621. [Google Scholar] [CrossRef]
  52. Kim, I.; Chin, Y.W.; Lim, S.W.; Kim, Y.C.; Kim, J. Norisoprenoids and hepatoprotective flavone glycosides from the aerial parts of Beta vulgaris var. cicla. Arch. Pharm. Res. 2004, 27, 600–603. [Google Scholar] [CrossRef]
  53. Cutillo, F.; D’Abrosca, B.; DellaGreca, M.; Fiorentino, A.; Zarrelli, A. Terpenoids and phenol derivatives from Malva silvestris. Phytochemistry 2006, 67, 481–485. [Google Scholar] [CrossRef]
  54. Machado, F.B.; Yamamoto, R.E.; Zanoli, K.; Nocchi, S.R.; Novello, C.R.; Schuquel, I.T.A.; Sakuragui, C.M.; Luftmann, H.; Ueda-Nakamura, T.; Nakamura, C.V.; et al. Evaluation of the antiproliferative activity of the leaves from Arctium lappa by a bioassay-guided fractionation. Molecules 2012, 17, 1852–1859. [Google Scholar] [CrossRef] [PubMed]
  55. Fiorucci, L.; Mantovanelli, G.C.; Bernardi, D.I.; Silva, A.A.; De Oliveira, R.S., Jr.; Ishii-Iwamoto, E.L.; Sarragiotto, M.H.; Baldoqui, D.C. Isolation of the constituents and evaluation of allelopathic potential of Raphanus sativus L. (Brassicaceae). Planta Med. 2014, 80, P1L61. [Google Scholar] [CrossRef]
  56. Mayer, H. Synthesis of optically active carotenoids and related compounds. Pure Appl. Chem. 1979, 51, 535–564. [Google Scholar] [CrossRef]
  57. Ren, Y.; Shen, L.; Zhang, D.; Dai, S. Two new sesquiterpenoids from Solanum lyratum with cytotoxic activities. Chem. Pharm. Bull. 2009, 57, 408–410. [Google Scholar] [CrossRef] [PubMed]
  58. Yang, X.; Kang, M.-C.; Lee, K.-W.; Kang, S.M.; Lee, W.W.; Jeon, Y.J. Antioxidant activity and cell protective effect of loliolide isolated from Sargassum ringgoldianum subsp. coreanum. Algae 2011, 26, 201–208. [Google Scholar] [CrossRef]
  59. Okada, N.; Shirata, K.; Niwano, M.; Koshino, H.; Uramoto, M. Immunosuppressive activity of a monoterpene from Eucommia ulmoides. Phytochemistry 1994, 37, 281–282. [Google Scholar] [CrossRef]
  60. Chung, C.-Y.; Liu, C.-H.; Burnouf, T.; Wang, G.H.; Chang, S.P.; Jassey, A.; Tai, C.; Tai, C.; Huang, C.; Richardson, C.; et al. Activity-based and fraction-guided analysis of Phyllanthus urinaria identifies loliolide as a potent inhibitor of hepatitis C virus entry. Antivir. Res. 2016, 130, 58–68. [Google Scholar] [CrossRef]
  61. Grabarczyk, M.; Winska, K.; Maczka, W.; Potaniec, B.; Anioł, M. Loliolide—The most ubiquitous lactone. Folia Biol. Oecol. 2015, 11, 1–8. [Google Scholar] [CrossRef]
  62. Dietz, H.; Winterhalter, P. Phytotoxic constituents from Bunias orientalis leaves. Phytochemistry 1996, 42, 1005–1010. [Google Scholar] [CrossRef]
  63. Bich, T.T.N.; Kato-Noguchi, H. Isolation and identification of a phytotoxic substance from the emergent macrophyte Centrostachys aquatica. Bot. Stud. 2014, 55, 59. [Google Scholar] [CrossRef]
  64. Zhou, B.; Kong, C.H.; Li, Y.H.; Wang, P.; Xu, X.H. Crabgrass (Digitaria sanguinalis) allelochemicals that interfere with crop growth and the soil microbial community. J. Agric. Food Chem. 2013, 61, 5310–5317. [Google Scholar] [CrossRef] [PubMed]
  65. Islam, M.S.; Iwasaki, A.; Suenaga, K.; Kato-Noguchi, H. Isolation and identification of two potential phytotoxic substances from the aquatic fern Marsilea crenata. J. Plant Biol. 2017, 60, 75–81. [Google Scholar] [CrossRef]
  66. Hossen, K.; Iwasaki, A.; Suenaga, K.; Kato-Noguchi, H. Phytotoxic activity and growth inhibitory substances from Albizia richardiana (Voigt.) King & Prain. Appl. Sci. 2021, 11, 1455. [Google Scholar]
  67. DellaGreca, M.; Fiorentino, A.; Monaco, P.; Previtera, L.; Temussi, F.; Zarrelli, A. New dimeric phenanthrenoids from the rhizomes of Juncus acutus. Structure determination and antialgal activity. Tetrahedron 2003, 59, 2317–2324. [Google Scholar] [CrossRef]
  68. Chengxu, W.; Mingxing, Z.; Xuhui, C.; Bo, Q. Review on allelopathy of exotic invasive plants. Procedia. Eng. 2011, 18, 240–246. [Google Scholar] [CrossRef]
  69. Lockwood, J.L.; Simberloff, D.; McKinney, M.L.; Holle, B.V. How many, and which, plants will invade natural areas. Biol. Invasions 2001, 3, 1–8. [Google Scholar] [CrossRef]
  70. Meiners, S.J.; Kong, C.H.; Ladwig, L.M.; Pisula, N.L.; Lang, K.A. Developing an ecological context for allelopathy. Plant Ecol. 2012, 213, 1861–1867. [Google Scholar] [CrossRef]
  71. Dayan, F.E.; Romagni, J.G.; Duke, S.O. Investigating the mode of action of natural phytotoxins. J. Chem. Ecol. 2000, 26, 2079–2094. [Google Scholar] [CrossRef]
  72. Kobayashi, M.; Ueda, M.; Furumoto, T.; Kawanami, Y. Retarding activity of 6-O-acyl-D-allose against plant growth. Biosci. Biotechnol. Biochem. 2010, 74, 216–217. [Google Scholar] [CrossRef]
  73. Cueva, C.; Moreno-Arribas, M.V.; Martinez-Alvarez, P.J.; Bills, G.; Vicente, M.F.; Basilio, A.; Lopez Rivas, C.; Requena, T.; Rodríguez, J.M.; Bartolomé, B. Antimicrobial activity of phenolic acids against commensal, probiotic and pathogenic bacteria. Res. Microbiol. 2010, 16, 372–382. [Google Scholar] [CrossRef]
  74. Sanchez-Maldonado, A.F.; Schieber, A.; Ganzle, M.G. Structure-function relationships of the antibacterial activity of phenolic acids and their metabolism by lactic acid bacteria. J. Appl. Microbiol. 2011, 111, 1176–1184. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Polygonum chinense.
Figure 1. Polygonum chinense.
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Figure 2. Effect of the Polygonum chinense above plant parts extracts on the seedling growth of alfalfa and Italian ryegrass at six concentrations. Each bar expresses mean ± SE with six replicates (n = 60). The letters on the bars signify significant differences (Tukey’s HSD test, at 0.05 probability level).
Figure 2. Effect of the Polygonum chinense above plant parts extracts on the seedling growth of alfalfa and Italian ryegrass at six concentrations. Each bar expresses mean ± SE with six replicates (n = 60). The letters on the bars signify significant differences (Tukey’s HSD test, at 0.05 probability level).
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Figure 3. Procedure for isolation and purification of allelopathic active compounds from the extracts of the above plant parts Polygonum chinense.
Figure 3. Procedure for isolation and purification of allelopathic active compounds from the extracts of the above plant parts Polygonum chinense.
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Figure 4. Effects of the distilled water (aqueous) and ethyl acetate (EtOAc) fractions on the seedling growth of cress obtained by partitioning the extracts of Polygonum chinense at the concentrations of 0.1 and 0.3 g DW equivalent extract/mL. Each bar expresses mean ± standard error with three replicates (n = 30). Different letters on the bars signify significant differences (Tukey’s HSD test, at 0.05 probability level).
Figure 4. Effects of the distilled water (aqueous) and ethyl acetate (EtOAc) fractions on the seedling growth of cress obtained by partitioning the extracts of Polygonum chinense at the concentrations of 0.1 and 0.3 g DW equivalent extract/mL. Each bar expresses mean ± standard error with three replicates (n = 30). Different letters on the bars signify significant differences (Tukey’s HSD test, at 0.05 probability level).
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Figure 5. The inhibitory effect of the P. chinense above plant parts extracts on the shoot and root growth of cress. The cress seeds were treated with different ratios of EtOAc in n-hexane (v/v) at the concentration of 0.6 g DW equivalent extract/mL using nine fractions and the last fraction eluted with MeOH. Each bar expresses mean ± standard error with three replicates (n = 30). *, **, *** Asterisks signify significant differences (Tukey’s HSD test at 0.05, 0.01, 0.001 probability level, respectively). NS: Non-significant differences.
Figure 5. The inhibitory effect of the P. chinense above plant parts extracts on the shoot and root growth of cress. The cress seeds were treated with different ratios of EtOAc in n-hexane (v/v) at the concentration of 0.6 g DW equivalent extract/mL using nine fractions and the last fraction eluted with MeOH. Each bar expresses mean ± standard error with three replicates (n = 30). *, **, *** Asterisks signify significant differences (Tukey’s HSD test at 0.05, 0.01, 0.001 probability level, respectively). NS: Non-significant differences.
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Figure 6. The structure of dehydrovomifoliol isolated from the above plant parts of P. chinense extract.
Figure 6. The structure of dehydrovomifoliol isolated from the above plant parts of P. chinense extract.
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Figure 7. Effects of dehydrovomifoliol against the growth of cress seedlings. Each bar expresses mean ± SE with three replicates (n = 30). Different letters on the bars signify significant differences, but any two means having a common letter are not significant differences within the group (Turkey’s HSD test, at 0.05 probability level).
Figure 7. Effects of dehydrovomifoliol against the growth of cress seedlings. Each bar expresses mean ± SE with three replicates (n = 30). Different letters on the bars signify significant differences, but any two means having a common letter are not significant differences within the group (Turkey’s HSD test, at 0.05 probability level).
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Figure 8. The structure of loliolide isolated from the above plant parts of P. chinense extract.
Figure 8. The structure of loliolide isolated from the above plant parts of P. chinense extract.
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Figure 9. Effects of loliolide against the growth of cress, alfalfa, and Italian ryegrass. Each bar expresses mean ± standard error with three replicates (n = 30). Different letters on the bars signify significant differences, and any two means having a common letter are not significant differences within the group (Turkey’s HSD test, at 0.05 probability level).
Figure 9. Effects of loliolide against the growth of cress, alfalfa, and Italian ryegrass. Each bar expresses mean ± standard error with three replicates (n = 30). Different letters on the bars signify significant differences, and any two means having a common letter are not significant differences within the group (Turkey’s HSD test, at 0.05 probability level).
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Table 1. Concentrations necessary for the P. chinense extracts to inhibit the seedling growth of the test plants by 50% (I50 values).
Table 1. Concentrations necessary for the P. chinense extracts to inhibit the seedling growth of the test plants by 50% (I50 values).
Test PlantI50 Value
(g DW Equivalent Extract/mL)
ShootRoot
Alfalfa0.00350.0049
Italian ryegrass0.00430.0052
Table 2. Concentrations required for dehydrovomifoliol to inhibit the growth of the cress seedling shoots and roots by 50% (I50 values).
Table 2. Concentrations required for dehydrovomifoliol to inhibit the growth of the cress seedling shoots and roots by 50% (I50 values).
Test PlantI50 Value (mM)
ShootRoot
Cress21.2
Table 3. Concentrations required for loliolide to inhibit the growth of the test plant seedlings by 50% (I50 values).
Table 3. Concentrations required for loliolide to inhibit the growth of the test plant seedlings by 50% (I50 values).
Test PlantI50 Value (mM)
ShootRoot
Cress0.150.33
Alfalfa2.332.23
Italian ryegrass0.801.90
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Lun, T.L.; Tojo, S.; Teruya, T.; Kato-Noguchi, H. Allelopathic Activity of the Invasive Plant Polygonum chinense Linn. and Its Allelopathic Substances. Plants 2023, 12, 2968. https://doi.org/10.3390/plants12162968

AMA Style

Lun TL, Tojo S, Teruya T, Kato-Noguchi H. Allelopathic Activity of the Invasive Plant Polygonum chinense Linn. and Its Allelopathic Substances. Plants. 2023; 12(16):2968. https://doi.org/10.3390/plants12162968

Chicago/Turabian Style

Lun, Thang Lam, Shunya Tojo, Toshiaki Teruya, and Hisashi Kato-Noguchi. 2023. "Allelopathic Activity of the Invasive Plant Polygonum chinense Linn. and Its Allelopathic Substances" Plants 12, no. 16: 2968. https://doi.org/10.3390/plants12162968

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