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Article

Evaluation of the Activity of Estragole and 2-Isopropylphenol, Phenolic Compounds Present in Cistus ladanifer

1
Department of Plant Biology, Ecology and Earth Sciences, Faculty of Science, University of Extremadura, 06006 Badajoz, Spain
2
Center for Scientific and Technological Research of Extremadura (CICYTEX), Department of Crop Protection, 06187 Badajoz, Spain
*
Author to whom correspondence should be addressed.
Agronomy 2022, 12(5), 1139; https://doi.org/10.3390/agronomy12051139
Submission received: 5 April 2022 / Revised: 5 May 2022 / Accepted: 6 May 2022 / Published: 9 May 2022
(This article belongs to the Special Issue Advances in Plant Allelopathy)

Abstract

:
A large number of studies of Cistus ladanifer highlight this Mediterranean shrub as a source of the phenolic compounds responsible for the allelopathic potential of this species. There are few phenolic compounds present in C. ladanifer that have not yet been studied. The objective of this work was to evaluate the activity of estragole and 2-isopropylphenol on filter paper and soil on monocotyledons (Allium cepa) and dicotyledons (Lactuca sativa). The results showed that when the test was carried out on paper, the germination and the growth of the L. sativa was strongly inhibited by 2 isopropylphenol and estragole. 2 isopropylphenol showed an IC50 on the germination of 0.7 mM and 0.1 mM on the germination rate, 0.4 mM on the size of radicle and 0.3 mM on the size of hypocotyl. Estragole showed an IC50 on the germination rate of 1.5 mM and 1.1 mM on the size of hypocotyl. The effects of these pure compounds on A. cepa were lower, and when the assays were performed on the soil, they were dissipated. The mixture of these compounds on A. cepa had 0.6 mM IC50 for the length hypocotyl on paper and 1.1 mM for the length of the radicle on soil. The mixture on L. sativa also inhibited the length of the radicle with an IC50 of 0.6 mM. On the other hand, it was also observed that estragole stimulated the growth of the A. cepa radicle length on soil, showing a hormetic effect with an EC50 of 0.1 mM. In conclusion, it can be said that for a species to be allelopathic in nature, it is essential to verify the effect of its possible allelochemicals on the target species, on the soil in which they will exert their action and at the concentrations found in their usual environment, in addition to taking into account the interaction with other compounds present in the medium.

1. Introduction

Plants show a vast variety of secondary metabolites, many of which with allelopathic effects. The way in which these compounds act is similar to that of synthetic herbicides, and their high variety offers the possibility to generate new sources of environmentally friendly herbicides with new mechanisms of action and unexplored target places [1]. In fact, the phenomena of allelopathy and phytotoxic interactions among plants mediated by allelochemicals are already being used in different ways, such as crop rotation, cover crops, dead mulches and aqueous extracts [2]. Phenolic compounds are widely known for being allelopathic [3]. It could be asserted that the phytotoxicity of phenolic compounds is well established, and therefore, they can be an important source of new herbicides [2,4,5].
In the Mediterranean region, the rockrose occupies large areas, often forming almost monospecific communities. It has been demonstrated that the allelopathic effect of Cistus ladanifer hinders the establishment of some shrubs and can reduce the area occupied by numerous herbaceous species, which can consequently influence the composition and structure of the communities in which this species is present [6]. The identification and evaluation of secondary metabolites with phytotoxic activity in leaves of Cistus ladanifer supports the relevance of allelopathy for the success of this species in this ecosystem [7,8,9,10,11,12]. The literature shows that some of these phytotoxic compounds are phenolic compounds and can prevent or delay germination and exert a negative influence on the radicles and hypocotyls of seedlings [6,7,9,10,13]. Such a combined allelopathic effect, i.e., reduction and/or delay of germination, along with the underdevelopment of the seedling, should have fatal consequences for the establishment of plants in semiarid Mediterranean environments [14], which would explain the reduction in the richness and diversity of herbaceous species in Mediterranean communities where it is present [15,16,17]. The aim of this study was to thoroughly evaluate the phytotoxic activity of phenolic compounds present in Cistus ladanifer that have not yet been evaluated and that may present suitable characteristics for use as bioherbicides. Few phenolic compounds remain present in C. ladanifer that have not yet been evaluated in isolation [7,8,12]. Two of them are estragole and 2-isopropylphenol, which are present in its leaves. These secondary metabolites are minor compounds from Cistus ladanifer essential oil [18,19,20,21,22]. Although these metabolites are also synthesized by other species, it is in Cistus ladanifer where we can find them together. In Cistus ladanifer, more than 350 compounds from different families have been identified. Research indicates that the allelopathic effect of this species is due to the combination of several compounds [8,9,10]. Additionally, this study of all the components present in this species can be revealing.
Estragole, 4-allylanisole or 1-methoxy-4-prop-2-enylbenzene, is found in many plant species, particularly in spices, and it is used in perfumes and as a flavoring in foods and liquors. This compound was first isolated from avocado rind (Persea gratissima Garth). It is the main compound of tarragon oil (Artemisia dracunculus L.), and its presence in a proportion of 60–75% can be the cause of the allelopathic activity of this species [23,24]. If released to the soil, estragole is expected to have low mobility. It exists as a liquid under environmental conditions; therefore, estragole may volatilize from dry soil. Utilizing the OECD 301F ready Biodegradability test, 48% O2 consumption was reached in 4 weeks, indicating that biodegradation may be an important environmental fate process in soil or water [25,26]. Despite all this information, the phytotoxic activity of this compound has never before been evaluated in isolation. For 2-isopropylphenol, o-cumenol or 2-propan-2-ylphenol, no information was found relative to these parameters [27], but the phenolic compounds of low molecular weight may have similar biodegradable characteristics.
To carry out an evaluation of these compounds with possible phytotoxic activity, there are standardized bioassays that allow evaluating the degree of affectation that a chemical substance produces in selected test organisms [28,29]. This implies evaluating the effect of the substance on the germination and growth of seedlings [30]. Thus, the aim of the present study was to carry out a bioassay in Petri dishes to evaluate the phytotoxic potential of estragole and 2-isopropylphenol.

2. Results

2.1. Effect of Phenolic Compounds on the Germination of Allium cepa and Lactuca sativa

In the tests carried out with Allium cepa on paper, the highest concentration (1 mM) of both estragole and 2-isopropylphenol showed a significantly inhibitory effect on germination rate (%GR). 2-isopropylphenol also showed a significantly inhibitory effect on germination (%GT). At the lowest concentration (0.1 mM), both compounds showed a significantly stimulating effect on these indices, whereas at 0.5 mM, no differences were observed with the control. In soil, these effects disappeared, and no significant differences were found with the control at any of the tested concentrations (Figure 1).
When the assay was carried out with Lactuca sativa on paper, 2-isopropylphenol strongly inhibited germination at 1mM, and the two compounds, separately, significantly inhibited the germination rate at all the tested concentrations, showing a significant positive correlation with concentration (R2 = 0.97 for estragole and R2 = 0.96 for 2-isopropylphenol). The effective concentration required to induce half maximal inhibition (IC50) of 2-isopropylphenol on lettuce germination was 0.7 mM, and on germination rate, it was 0.1 mM for 2-isopropylphenol and 1.5 mM for estragole. As in the case of Allium cepa in soil, the effect disappeared, and we only observed a significant inhibition of germination rate with 2-isopropylphenol at 1 mM (Figure 2).
When tested with the mixture of the two compounds on paper, the concentration of 1mM showed total inhibition of germination in Lactuca sativa and inhibition of over 45% of germination in Allium cepa. At 0.5mM, there was also significant inhibition of germination and germination rate in Lactuca sativa and of germination rate in Allium cepa. Moreover, at 0.1 mM, there was also significant inhibition of germination rate in Lactuca sativa. At 0.1mM, the joint action of the two compounds showed a hormetic effect on Allium cepa, observing the same stimulating effect detected with the pure compounds on %GT and %GR. It is worth highlighting that the joint action of the two compounds at 0.5mM significantly inhibited %GR in A. cepa, and %GT and %GR in L. sativa, while such inhibition was not observed when the compounds were tested separately. Furthermore, in the rest of the treatments performed, this inhibition was significantly greater than that observed when these compounds acted alone. Likewise, when the test was conducted in soil, the effects observed on paper disappeared. In soil, when these compounds acted separately, they did not significantly inhibit %GR in Lactuca sativa at 0.5 mM, although their mixture did show a significant inhibition of %GR and, in addition, at 1mM, such inhibition of %GR was significantly greater than that observed with the pure compounds (Figure 1 and Figure 2).

2.2. Effect of Phenolic Compounds on the Seedling Growth of Allium cepa and Lactuca sativa

Regarding the radicle and shoot length, when the assay was conducted with Allium cepa, on paper, it was observed that both estragole and 2-isopropylphenol significantly inhibited the radicle size (%Radicle length) at all the tested concentrations. These compounds also significantly inhibited the hypocotyl size (%Hypocotyl length) at 0.5 and 1 mM, although at 0.1 mM, estragole did not show any effect, and 2-isopropylphenol significantly stimulated hypocotyl growth. In soil, 2-isopropylphenol only significantly inhibited radicle and hypocotyl size at the highest concentration (1 mM). The inhibition of hypocotyl size shown by estragole on paper disappeared in soil, and the effect on the radicle was the opposite of that observed on paper, showing a significant stimulation of radicle growth that was significantly greater at lower concentration (R2 = 0.98), showing an EC50 of 0.1mm (Figure 3).
When the assay was conducted with Lactuca sativa on paper, estragole significantly inhibited radicle size at 1 mM and hypocotyl size at all the tested concentrations, showing a significant positive correlation with concentration (R2 = 0.98). In this case, the concentration of estragole needed to inhibit the length of hypocotyl by 50% was greater than 1 mM. On paper, 2-isopropylphenol also significantly inhibited radicle and hypocotyl size at all the tested concentrations, showing a significant positive correlation (R2 = 0.98 and R2 = 0.97, respectively). The IC50 of 2-isopropylphenol on lettuce radicle size was 0.4 mM, and on hypocotyl size it was 0.3 mM. When the assay was carried out in soil, the radicle size was not affected by any of the two compounds at any of the tested concentrations, and, although the inhibitory effect on the hypocotyls was lower than that observed on paper, the hypocotyl length was negatively affected by both compounds at all the tested concentrations, except for estragole at 0.5 mM (Figure 4).
When tested with the mixture of the two compounds (Figure 3 and Figure 4), in both paper and soil, there was a significant inhibition of radicle and hypocotyl growth in Allium cepa at 0.5 and 1 mM, and of radicle size at 0.1 mM on paper, with the latter inhibition being greater at the highest concentration (1 mM). When the test was performed on paper, a significant positive correlation was observed with the concentration for the length of the hypocotyl (R2 = 0.98) with an IC50 of 0.6 mM. When the test was performed in soil, a significant positive correlation was also observed with the concentration for the length of the radicle (R2 = 0.98) with an IC50 of 1.1 mM. It is worth highlighting that in soil, although estragole at 1mM did not show any effect on its own on radicle and hypocotyl size, the joint action of the two compounds did, with the latter inhibition being significantly greater that that observed with pure 2-isopropylphenol. Similarly, when the assay was conducted with Lactuca sativa, both radicle and hypocotyl length was significantly inhibited in both soil and paper, at all the tested concentrations, except for radicle length at the lowest concentration (0.1 mM). This inhibition was greater at the highest concentration, showing a significant positive correlation with concentration for radicle length when the assay was performed on paper (R2 = 0.96). In this case, the concentration of the mixture of compounds needed to inhibit the length of the radicle by 50% was 0.6mM.

3. Discussion

As sessile organisms, plants cannot escape the environment in which they germinate and thus have developed a series of strategies to defend themselves against biotic and abiotic stresses. Secondary metabolites are an essential part of such strategies, as they protect from UV rays and act as antimicrobials, repellents and anti-competitors or allelochemicals [31]. There are a variety of phenolic compounds of plants with allelopathic effects, many of which have shown a promising activity in weed control. Simple phenolic compounds have low molecular weight, which implies rapid degradation and prevents their accumulation in the soil and their possible influence on non-target organisms. They are water soluble, which facilitates their application without the need for surfactants [32,33]. Moreover, due to their high diversity with specific properties, they are promising tools in the discovery of new specific target places in weeds [5]. Therefore, these natural compounds can represent a large field for the discovery of new herbicides that are safe for humans, animals and the environment.
The phytotoxic activity of two phenolic compounds, viz., estragole and 2-isopropylphenol, which has never been studied before, was undertaken in this study. The results showed that these compounds presented phytotoxic activity to a lesser or greater extent depending on the substrate, the species and the tested concentration. On paper, 2-isopropylphenol at 1mM inhibited the germination of Lactuca sativa almost entirely. Several studies have shown that phenolic compounds can directly inhibit germination; for instance, chlorogenic acid, caffeic acid and catechol inhibit germination, as they alter the functioning of the enzyme λ-phosphorylase, which is clearly related to seed germination [5,34]. The results showed that estragole and 2-isopropylphenol also significantly inhibited germination rate and growth in the shoot and radicle of Lactuca sativa at the three tested concentrations on paper, observing that the higher the concentration, the greater the germination delay and the lesser the development of the seedlings. This effect on radicle growth can have equally negative consequences for any species to settle in natural conditions [15]. Previous studies show that some phenolic acids also present in Cistus ladanifer and at similar concentrations have the same effect on seed germination and seedling growth [7,9,10,31,35]. Pearson’s determination analysis indicated that the concentration of these compounds is correlated with the tested concentrations. 2-Isopropylphenol showed an IC50 of 0.7 mM on the germination, 0.1 mM on the rate of germination, 0.4 mM on radicle size and 0.3 mM on hypocotyl size, and an IC50 of estragole on the germination rate was 1.5 mM and 1.1 mM on the size of hypocotyl of Lactuca sativa. All of this suggests that these phytochemicals can be a potential source of bioherbicides [36]. Estragole is the main compound of tarragon oil (Artemisia dracunculus L.) and, therefore, can be the cause of the allelopathic activity of this species.
However, when the experiment was conducted in soil, the effect was weaker, and these compounds did not affect germination directly, observing inhibition only on germination rate with 2-isopropylphenol at 1 mM. On the other hand, there was significant inhibition of hypocotyl size at the three concentrations tested. In the tests conducted in soil, the activity of compounds may have been altered due to chemical losses and transformations, which could explain why the effect in soil was weaker. The microorganisms present in the soil may also play an important role in dissipating the effect of these compounds on this substrate [37,38].
In the assay conducted with Allium cepa, the phytotoxic effect of these compounds was weaker than that observed on Lactuca sativa. In addition, it is worth highlighting that the behavior was also different. On paper, total germination, germination rate and seedling development were significantly inhibited at the highest concentration (1 mM), although at low concentration (0.1 mM), it was observed that germination and germination rate were significantly stimulated by both compounds separately; moreover, 2-isopropylphenol also stimulated hypocotyl growth at that concentration. When the assay was carried out with Allium cepa in soil, the effects were weaker, and significant inhibition was only observed in radicle and hypocotyl size with 2-isopropylphenol at 1 mM. It was also observed that radicle growth was significantly stimulated at low concentrations of estragole (0.5 and 0.1 mM). As was stated by Bhowmik and Inderjit (2003), the effects of one plant on another plant can be either stimulating or inhibitory depending on the concentration of the released compounds [39]. This dose-dependent activity has been observed in other phenolic compounds that are also present in Cistus ladanifer, such as benzoic acid and p-hydroxybenzoic acid, with a stimulating effect at low concentrations (0.01 mM) [40]. Most allelochemicals can produce inhibitory effects at higher concentrations and stimulate growth when used at low concentrations [41]. This stimulating effect on the analyzed parameter is known as hormesis [42]. This effect can produce an average stimulation of 30–60% with respect to the control [43,44,45]. The application of phytotoxic compounds at low doses improves the physiological processes (including photosynthesis and respiration) and increases oxygen absorption, stomatal conductance and the water content of leaves, among other parameters [46,47]. Therefore, these compounds could also be used to enhance the growth of crop plants. Belz et al. (2009) demonstrated that, in soil, the degradation of toxic doses of allelochemicals can lead to low concentrations that may cause hormesis on plant growth [48]. The nutritional stress, together with factors such as the microorganisms, texture and physical and chemical properties of the soil, can also be one of the causes underlying the difference observed between the assay performed on paper (substrate without nutrients) and the one conducted in soil (commercial substrate with an optimal amount of nutrients).
Generally, in the phenomena of allelopathy or phytotoxic interactions among plants, several compounds are involved, and it is the combination of two or more allelochemicals that enables such activity [49]. Attacking weeds simultaneously with several allelopathic compounds with different mechanisms of action can stop resistance phenomena [28]. Thus, it is always interesting to evaluate the combination of compounds that are synthesized in the same species. In the present study, the results showed that the mixture of estragole and 2-isopropylphenol significantly inhibits germination percentage, germination rate and shoot and radicle growth in Lactuca sativa at the three concentrations tested on paper, observing that the higher concentration, the greater the germination delay and the lesser the seedling development. As in the case of the pure compounds, when the experiment was conducted in soil, the effect was weaker, although the mixture at 0.5 mM significantly inhibited germination rate, and at 0.5 and 1 mM it inhibited radicle size, whereas each of the compounds on their own did not show such effects. The mixture on L. sativa also inhibits the length of the radicle with an IC50 of 0.6 mM. On the other hand, it was also observed that estragole stimulated the growth of the A. cepa radicle length in soil showing a hormetic effect with an EC50 of 0.1 mM. When the assay was conducted with Allium cepa on paper, the same inhibitory and hormetic effects as those of the pure compounds were observed at high and low doses, respectively; however, when the assay was performed with this species in soil, the mixture inhibited shoot and radicle development to a greater extent with respect to the pure compounds. This is in line with numerous studies, which show that combinations of phenolic compounds present a greater phytotoxic activity compared to the same compounds on their own [7,29,31,50,51]. Mixtures of allelochemical compounds have shown a more effective inhibition of growth than each of the individual compounds separately at medium and high concentrations (0.1 and 1 mM) [40,52]. This behavior could suggest that in order for these compounds to be active, it is not necessary for them to be present at high concentrations in the medium in which they exert their action [10,53,54,55].
Several studies state that the extract of Cistus ladanifer presents a large diversity of secondary metabolites with phytotoxic activity, establishing and supporting the hypothetical relevance of allelopathy to its success in the habitats of the Mediterranean ecosystem in which it is present [8,12]. However, this proposed preliminary hypothesis of allelopathically mediated defense against other plants may not be the only rationale for all its secondary metabolites. The observation of compounds with a hormetic effect implies that some of these compounds may also play a role in growth regulation in the producing plant itself [56]. Nutrient imbalance is one of the main causes of stress in plants in natural conditions, and Cistus ladanifer is usually found in poor soils. Lehman and Blum (1999) reported that in the conditions of nutritional stress, the application of ferulic acid at 0.2mM increased phosphorus absorption in cucumbers (Cucumis sativa L) [57]. Different works identify other compounds, such as cinamic acid, in addition to ferulic, as potential stimulators of herbaceous growth [57,58,59]. These compounds are present in C. ladanifer. Therefore, the success of this species could be due not only to a good control of competitors through the synthesis of allelopathic compounds but also to the stimulation of hormonal growth of these compounds on the individuals that constitute the rockrose population.
Studies that explored weed control using aqueous extracts of different crops found a significant increase in crop yield [60,61,62,63]. This increase could be due to a good weed control, resulting in a lower competition of the crop plants with weeds, although it could also be due to the stimulation of the hormonal growth in the crop plants. Thus, although the secondary metabolites of plants continue to be a potential source for the development of natural herbicides, it is also necessary to pay attention to the hormetic effects that they may present at low concentrations. Most studies on phytotoxicity are conducted in laboratory conditions to remove other factors derived from the properties of the soil. Such approach allows recognizing only the direct effects of allelochemical action. There is still great need for transferring the laboratory data to the field conditions. In fact, the concentrations at which the allelochemicals are found in field conditions are usually lower than those at which these compounds showed phytotoxic activity. In the framework of a wider selection aimed at identifying more environmentally friendly tools and management strategies for the creation of a more sustainable agriculture, the hormetic effect of allelopathic compounds may have a greater practical potential compared to their inhibitory potential. It would be ideal to find allelochemicals that, when applied in the field at the beginning of the cultivation process in sufficient amounts to control the growth of weeds, would then degrade to doses that improve the crop yield. On the other hand, it should be noted that the application of high concentrations of any compound in the soil can be harmful to the environment and human health. The exposure to estragole resulting from consumption of herbal medicinal products (short-time use in adults at the recommended posology) does not pose a significant cancer risk, but at high concentrations, it can be carcinogenic and genotoxic [64].
From the present study, we can conclude that the effect of the tested allelochemicals can vary depending on the substrate, the dose and the tested species, therefore corroborating with other studies [65,66]. For this reason, it can be pointed out that in the study of allelopathy or the search for new herbicides, in order to draw conclusions about what really occurs in the ecosystem in which the species is found or to know what will occur in the cultivated soil where the allelochemical will be applied, it is necessary: (a) to carry out studies with different species, in order to clarify the specificity of the compound; (b) to use a range of concentrations that show possible phytotoxic and hormetic effects; (c) to reproduce in the experiment the physical–chemical and biological properties of the natural environment; (d) to approach the study while taking into account the presence of other compounds that can enhance the activity of these compounds. In addition, all of this, and especially the last point, can help in finding alternatives to the phenomenon of weed resistance.

4. Materials and Methods

4.1. Plant and Substrate Sources

We analyzed variables such as the effect of the compounds, separately and in combination, on two receptor species: Allium cepa and Lactuca sativa, representatives of mono- and di-cotyledoneae plants. These species are ideal for adequately showing the allelochemical effects on the germination processes [67,68]. Moreover, Lactuca sativa is recommended by the United States Environmental Protection Agency (US EPA) for phytotoxicity tests, being among the most sensitive species [69]. Allium cepa has proved to be the most useful and has repeatedly been suggested as a standard test material in the list of species historically used in plant testing by the International Organization for Standardization [70] and by the Organisation of Economic Cooperation and Development [71].
To carry out the bioassay, seeds of Lactuca sativa variety romaine verte maraîchère (Vilmorin Jardin—CS70110—38291 St Quentin Fallavier Cedex—France) and Allium cepa variety bianca di maggio (Vilmorin Jardin—CS70110—38291 St Quentin Fallavier Cedex—France) were used as representatives of dicotyledons and monocotyledons, respectively. The total germination of these seeds was over 98%.
The activity of the allelochemicals was carried out on Whatman No. 118 paper and a commercial substrate of universal type prepared based on 95% peat, 5% green compost and 1.3 Kg/m3 fertilizer: 12N + 12P + 17K (Geolia, Aki Bricolage España S.L. B-839857—Madrid, Spain). The commercial universal soil presented the following characteristics: organic matter per dry matter (60%), electrical conductivity (40 mS/m), apparent dry density (320 g/L), grain size (0–20 mm) and pH 5.5–6.5.
The activity of the allelochemicals can vary according to the planting substrate. For this reason, the experiment was carried out on Whatman No. 118 paper and on a commercial substrate. The commercial universal soil presented the following characteristics: organic matter per dry matter (60%), electrical conductivity (40 mS/m), apparent dry density (320 g/L), grain size (0–20 mm) and pH 6.5.
None of the materials (seeds and substrate) was sterilized before the experiment.

4.2. Phytotoxic Activity Test

Chemically pure reagents (estragole and 2-isopropylphenol of >98% purity) were obtained from Aldrich-Chemical. Different solutions were prepared with Milli-Q water from each component separately. The highest concentration was 1 mM, which is the maximum recommended concentration in allelopathic bioassays [35]. The minimum concentration was 0.1 mM, which was the lowest concentration for observing the dissipation of the effect of these compounds. In addition, solutions of 0.5 mM were also prepared. For the mixture of the two phenols, three solutions were prepared with equimolar concentrations of each of the compounds at 1 mM, 0.5 mM and 0.1 mM. To eliminate the effects of pH, we measured these parameters for each solution. The pH varied between 6.1 and 6.3 from one solution to another. There were no significant differences in pH among solutions.
In Petri dishes (four replicates for each experience), 50 seeds (200 in total) of Lactuca sativa or Allium cepa were placed on paper or 25 g of commercial substrate and watered with the different solutions prepared (5 mL for paper plates and 16 mL for soil). Control plates were watered with Milli-Q water. The plates were kept in a culture chamber at 22 °C for a photoperiod of 15 h of light and 9 h of darkness (5 days for L. sativa plates and 6 days for A. cepa plates).

4.3. Measured Indices to Quantify the Phytotoxic Effect

Germinated seeds were counted daily, and total germination (%TG) [7] and germination rate (%GR) [69,70] were calculated. On the last day of the experiment, 10 seedlings were chosen at random, and the length of the radicle and shoot was measured [72]. All results were expressed as a percentage relative to the control.

4.4. Statistical Analysis

The significance level of the comparisons among treatments was estimated using the Mann–Whitney U-test. The differences were considered significant when p < 0.05. The interrelationships between germination and seed growth with the concentration of phenolic compounds were determined by Pearson’s determination coefficient. The effective concentrations required to induce half maximal inhibition (IC50) or half maximal stimulation (EC50) of growth were calculated according to the linear relationship between concentration and per cent inhibition or stimulation of plant growth. All statistical analyses were conducted using the statistical software SPSS 15.0.1.

Author Contributions

Conceptualization, T.S.; methodology, E.R.; validation, T.S., A.d.R.S. and D.O.; formal analysis, E.R.; investigation, E.R. and T.S.; resources, T.S. and A.d.R.S.; data curation, D.O.; writing—original draft preparation, T.S.; writing—review and editing, E.R.; visualization, A.d.R.S. and D.O.; supervision, D.O.; project administration, A.d.R.S.; funding acquisition, T.S. and A.d.R.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Regional Government of Extremadura and the European Regional Development Fund, grants number GR18078 and IB18105.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. 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]
  2. Blanco, Y. La utilización de la alelopatía y sus efectos en diferentes cultivos agrícolas. Cultiv. Trop. 2006, 27, 5–16. Available online: https://www.redalyc.org/articulo.oa?id=193215825001 (accessed on 25 September 2021).
  3. Kuiters, A.T. Effects of phenolic acids on germination and early growth of herbaceous woodland plants. J. Chem. Ecol. 1989, 15, 467–479. [Google Scholar] [CrossRef] [PubMed]
  4. Muller, C.H. The Role of Allelopathy and the Evolution of Vegetation. In Biochemical Coevolution; Oregon States University Press: Corvaillis, OR, USA, 1970; pp. 13–32. [Google Scholar]
  5. Einhelling, F.A. Allelopathy: Current Status and Future Goals. In Allelopathy: Organisms, Processes, and Applications; Inderjit, K.M., Dakshini, M., Einhelling, F.A., Eds.; American Chemical Society: Washington, DC, USA, 1995; pp. 1–24. [Google Scholar]
  6. Herranz, J.M.; Farrandis, P.; Copete, M.A.; Duro, E.M.; Zalacaín, A. Effect of allelopathic compounds produced by Cistus ladanifer on germination of 20 Mediterranean taxa. Plant Ecol. 2006, 184, 259–272. [Google Scholar] [CrossRef]
  7. Tena, C.; Santiago, A.d.R.; Osuna, D.; Sosa, T. Phytotoxic Activity of p-Cresol, 2-Phenylethanol and 3-Phenyl-1-Propanol, Phenolic Compounds Present in Cistus ladanifer L. Plants 2021, 10, 1136. [Google Scholar] [CrossRef]
  8. Chaves, N.; Alías, J.C.; Sosa, T. Phytotoxicity of Cistus ladanifer L.: Role of allelopathy. Allelopath. J. 2016, 38, 113–132. [Google Scholar]
  9. Chaves, N.; Sosa, T.; Alías, J.C.; Escudero, J.C. Identification and effects of interaction phytotoxic compounds from exudate of Cistus ladanifer leaves. J. Chem. Ecol. 2001, 27, 3. [Google Scholar]
  10. Chaves, N.; Sosa, T.; Escudero, J.C. Plant growth inhibiting flavonoids in exudate of Cistus ladanifer and in associated soils. J. Chem. Ecol. 2001, 27, 623–631. [Google Scholar] [CrossRef]
  11. Chaves, N.; Ríos, J.L.; Gutiérrez, C.; Escudero, J.C.; Olías, J.M. Analysis of secreted flavonoids of Cistus ladanifer L. by high- performance liquid chromatography-particle beam mass spectrometry. J. Chromatogr. A 1998, 799, 111–115. [Google Scholar] [CrossRef]
  12. Dias, A.S.; Costa, C.T.; Dias, L.S. Allelopathic Plants. XVII. Cistus Ladanifer L. Allelopath. J. 2005, 16, 1–30. [Google Scholar]
  13. Verdeguer, M.; Blázquez, M.A.; Boira, H. Chemical composition and herbicidal activity of the essential oil from a Cistus ladanifer L. population from Spain. Nat. Prod. Res. Former. Nat. Prod. Lett. 2012, 26, 1602–1609. [Google Scholar]
  14. Muller, C.H.; Hanawalt, R.B.; McPherson, J.K. Allelopathic control of herb growth in the fire cycle of Californian chaparral. Bull. Torrey Bot. Club 1968, 95, 225–231. [Google Scholar] [CrossRef]
  15. Malato-Belíz, J.; Escudero, J.C.; Buyolo, T. Application of traditional indices and of diversity to an ecotonal area of different biomes. In The State of the Art in Vegetation Science; International Association for Vegetation Science (IAVS): Toledo, Spain, 1992; Volume 75. [Google Scholar]
  16. Ruiz, J. Matorrales. Tratado del Medio Natural; Ramos, J.L., Ed.; Universidad Politécnica de Madrid: Madrid, Spain, 1981; Volume 2, pp. 501–541. [Google Scholar]
  17. López-González, G. Los Árboles y Arbustos de la Península Lbérica E Islas Baleares; Mundi-Prensa: Madrid, Spain, 2001. [Google Scholar]
  18. Regino, J.M.B.; Frazio, S.; Canno, M.M.; Venancio, F. Estudo-da Parte Volátil do Concreto de Esteva; Jornadas Nacionais de Plantas Aromáticas e Óleos Essenciais: Lisboa, Portugal, 1987; pp. 81–99. [Google Scholar]
  19. Guy, I.; Vernin, G. Minor Compounds from Cistus ladaniferus L. Essential Oil from Esterel. 2. Acids and Phenols. J. Essent Oil Res. 1996, 8, 455–462. [Google Scholar] [CrossRef]
  20. Warnecke, H.-U. Constituents of the Essential Oil of Cistus Ladaniferus (Acids and Phenols). Dragoco Rep. 1978, 9, 192–195. [Google Scholar]
  21. Proksch, P.; Gülz, P.-G.; Budzikiewicz, H. Phenylpropanoic Acid Esters in the Essential Oil of Cistus ladanifer L. (Cistaceae). Z. Naturforsch. 1980, 35, 201–203. [Google Scholar]
  22. Vernin, G. Mass spectra and Kovats indices of some phenylpropanoic acid esters found in the essential oil of Cistus ladaniferus L. J. Essent. Oil Res. 1993, 5, 563–569. [Google Scholar] [CrossRef]
  23. Tak, I.R.; Mohiuddin, D.; Ganai, B.A.; Chishti, M.Z.; Ahmad, F.; Dar, J.S. Phytochemical studies on the extract and essential oils of Artemisia dracunculus L. (Tarragon). Afr. J. Plant Sci. 2014, 8, 72–75. [Google Scholar]
  24. Fraternalea, D.; Flaminib, G.; Riccia, D. Essential Oil Composition and Antigermination Activity of Artemisia dracunculus (Tarragon). Nat. Prod. Commun. 2015, 10, 1469–1472. [Google Scholar] [CrossRef] [Green Version]
  25. National Center for Biotechnology Information. PubChem Compound Summary for CID 8815, Estragole. Available online: https://pubchem.ncbi.nlm.nih.gov/compound/Estragole (accessed on 8 September 2021).
  26. ECHA. Search for Chemicals. 1-methoxy-4-(2-propenyl) benzene (140-67-0) Registered Substances Dossier. Available online: https://echa.europa.eu/ (accessed on 25 September 2021).
  27. National Center for Biotechnology Information. PubChem Compound Summary for CID 6943, 2-Isopropylphenol. Available online: https://pubchem.ncbi.nlm.nih.gov/compound/2-Isopropylphenol (accessed on 8 September 2021).
  28. Oliveros-Bastidas, A.J.; Rodríguez-Hernández, D.C.; Calcagno-Pissarelli, M.P. Estandarización de un bioensayo para la búsqueda de compuestos fitotóxicos en extractos vegetales. Ciencia 2011, 19, 187–202. [Google Scholar]
  29. Kapanen, A.; Itavaara, M. Ecotoxicity tests for compost applications. Ecotoxicol. Environ. Saf. 2001, 49, 1–16. [Google Scholar] [CrossRef]
  30. Haugland, E.; Brandsaeter, L.O. Experiments on bioassay sensitivity in the study of allelopathy. J. Chem. Ecol. 1996, 22, 1845–1859. [Google Scholar] [CrossRef] [PubMed]
  31. Viña, S.; Ringuelet, J. Compuestos fenólicos. In Productos Naturales Vegetales; Edulp Integra la Red de Editoriales Universitarias Nacionales (REUN): Buenos Aires, Argentina, 2013. [Google Scholar]
  32. Dayan, F.; Cantrell, C.; Duke, S. Natural product in crop protection. Bioorganic Med. Chem. 2009, 17, 4022–4034. [Google Scholar] [CrossRef] [PubMed]
  33. Vyvyan, J. ChemInform Abstract: Allelochemicals as Leads for New Herbicides and Agrochemicals. Tetrahedron 2002, 58, 1631–1646. [Google Scholar] [CrossRef]
  34. Rice, E.L. Allelophatic; Academic Press: Orlando, FL, USA, 1984. [Google Scholar]
  35. Kuuluvaine, T. Gap disturbance, ground microtopography, and the regeneration dynamics of boreal coniferous forest in Finland: A review. Ann. Zool. Fenn. 1994, 31, 35–51. [Google Scholar]
  36. Ghimire, B.K.; Hwang, M.H.; Sacks, E.J.; Yu, C.Y.; Kim, S.H.; Chung, I.M. Screening of allelochemicals in Miscanthus sacchariflorus extracts and assessment of their effects on germination and seedling growth of common weeds. Plants 2020, 9, 1313. [Google Scholar] [CrossRef] [PubMed]
  37. Desai, S.M.; Govind, R.; Tabak, H.H. Development of quantitative structure—Activity relationships for predicting biodegradation kinetics. Environ. Toxicol. Chem. 1990, 9, 473–477. [Google Scholar] [CrossRef]
  38. Van Agteren, M.H.; Keuning, S.; Janssen, D. Handbook on Biodegradation and Biological Treatment of Hazardous Organic Compounds; Springer: Dordrecht, The Netherlands, 1998. [Google Scholar]
  39. Bhowmik, P.C.; Inderjit. Challenges and opportunities in implementing allelopathy for natural weed management. Crop Protect. 2003, 22, 661–671. [Google Scholar]
  40. Bouhaouel, I.; Richard, G.; Fauconnier, M.L.; Ongena, M.; Franzil, L.; Gfeller, A.; Amara, H.S.; du Jardin, P. Identification of barley (Hordeum vulgare L. subsp. vulgare) root exudates allelochemicals, their autoallelopathic activity and against Bromus diandrus Roth. Germination. Agronomy 2019, 9, 345. [Google Scholar] [CrossRef] [Green Version]
  41. Li Liu, D.; An, M.; Johnson, I.R.; Lovett, J.V. Mathematical modeling of allelopathy. III. A model for curve-fitting allelochemical dose responses. Nonlinearity Biol. Toxicol. Med. 2003, 1, 37–50. [Google Scholar] [CrossRef] [Green Version]
  42. Calabrese, E.J. Paradigm lost, paradigm found: The re-emergence of hormesis as a fundamental dose response model in the toxicological sciences. Environ. Pollut. 2005, 138, 378–411. [Google Scholar] [CrossRef]
  43. Calabrese, E.J. Hormesis: Why it is important to toxicologists and toxicology. Environ. Toxicol. Chem. 2008, 27, 1451–1471. [Google Scholar] [CrossRef] [PubMed]
  44. Calabrese, E.J. Hormesis is central to toxicology, pharmacology and risk assessment. Hum. Exp. Toxicol. 2010, 29, 249–261. [Google Scholar] [CrossRef] [PubMed]
  45. Belz, R.G.; Cedergreen, N.; Duke, S.O. Herbicide hormesisecan it be useful in crop production? Weed Res. 2011, 51, 321–332. [Google Scholar] [CrossRef]
  46. Kaya, C.; Tuna, A.L.; Yokas, I. The role of plant hormones in plants under salinity stress. In Salinity and Water Stress: Improving Crop Efficiency; Ashraf, M., Ozturk, M., Athar, H.R., Eds.; Springer: Berlin/Heidelberg, Germany, 2009; pp. 45–50. [Google Scholar]
  47. Yu, J.Q.; Ye, S.F.; Zhan, M.F.; Hu, W.H. Effects of root exudates and aqueous root extracts of cucumber (Cucumis sativus) and allelochemicals, on photosynthesis and antioxidant enzymes in cucumber. Biochem. Syst. Ecol. 2003, 31, 129–139. [Google Scholar] [CrossRef]
  48. Belz, R.G.; Van der Laan, M.; Reinhardt, C.F.; Hurle, K. Soil degradation of parthenind does it contradict the role of allelopathy in the invasive weed Parthenium hysterophorus L.? J. Chem. Ecol. 2009, 35, 1137–1150. [Google Scholar] [CrossRef]
  49. Blum, U.; Shafer, S.R.; Lehman, M.E. Evidence for inhibitory allelopathic interactions involving phenolic acids in field soils: Concepts vs. an experimental model. Crit. Rev. Plant Sci. 1999, 18, 673–693. [Google Scholar] [CrossRef]
  50. Liu, D.L.; Lovett, J.V. Biologically active secondary metabolites of barley. II. Phytotoxicity of barley allelochemicals. J. Chem. Ecol. 1993, 19, 2231–2244. [Google Scholar] [CrossRef]
  51. Hura, T.; Dubert, F.; Dabkowska, T.; Stupnicka-Rodzynkiewicz, E.; Stoklosa, A.; Lepiarczyk, A. Quantitative analysis of phenolics in selected crop species and biological activity of these compound sevaluated by sensitivity of Echinochloa crus-Gall. Acta Physiol. Plant. 2006, 28, 537–545. [Google Scholar] [CrossRef]
  52. Inderjit; Nilsen, E.T. Bioassays and field studies for allelopathy in terrestrial plants: Progress and problems. Crit. Rev. Plant Sci. 2003, 22, 221–238. [Google Scholar] [CrossRef]
  53. Dakshini, K.M.M. Formononetin 7-O-glucoside (ononin), an additional inhibitor in soils associated with the weed, Pluchea lanceolata (DC.) C. B. Clarke (Asteraceae). J. Chem. Ecol. 1992, 18, 713–718. [Google Scholar]
  54. Lehman, M.E.; Blum, U.; Gerig, T.M. Simultaneous effects of ferulic and p-coumaric acids on cucumber leaf expansion in split-root experiments. J. Chem. Ecol. 1994, 20, 1773–1782. [Google Scholar] [CrossRef] [PubMed]
  55. Sosa, T.; Valares, C.; Alías, J.C.; Chaves, N. Persistence of flavonoids in Cistus ladanifer soils. Plant Soil 2010, 377, 51–63. [Google Scholar] [CrossRef]
  56. Macías, F.A.; Oliveros-Bastidas, A.; Marín, D.; Carrera, C.; Chinchilla, N.; Molinillo, J.M.G. Plant biocommunicators: Their phytotoxicity, degradation studies and potential use as herbicide models. Phytochem. Rev. 2007, 7, 179–194. [Google Scholar] [CrossRef]
  57. Lehman, M.E.; Blum, U. Influence of pretreatment stresses on inhibitory effects of ferulic acid, an allelopathic phenolic acid. J. Chem. Ecol. 1999, 25, 1517–1529. [Google Scholar] [CrossRef]
  58. Wang, X.; Wang, H.; Wu, F.; Liu, B. Effect of cinnamic acid on physiological chahracteristics of cucumber seedlings under salt stress. Front. Agric. China 2007, 1, 58–61. [Google Scholar] [CrossRef]
  59. Abbas, T.; Nadeem, M.A.; Tanveer, A.; Chauhan, B.S. Can hormesis of plant-released phytotoxins be used to boost and sustain crop production? Crop Prot. 2017, 93, 69–76. [Google Scholar] [CrossRef]
  60. Cheema, Z.A.; Khaliq, A.; Akhtar, S. Use of sorgaab (sorghum water extract) as a natural weed inhibitor in spring mungbean. Int. J. Agric. Biol. 2001, 3, 515–518. [Google Scholar]
  61. Ashraf, M.; Akhlaq, M. Effects of sorghum leaves, roots and stems water extract, hand weeding and herbicide on weeds suppression and yield of wheat. Sarhad J. Agric. 2007, 23, 321–327. [Google Scholar]
  62. Jamil, M.; Cheema, Z.A.; Mushtaq, M.N.; Farooq, M.; Cheema, M.A. Alternative control of wild oat and canary grass in wheat fields by allelopathic plant water extracts. Agron. Sustain. Dev. 2009, 29, 475–482. [Google Scholar] [CrossRef]
  63. Khan, E.A.; Khakwani, A.A.; Ghazanfarullah, A. Effects of allelopathic chemicals extracted from various plant leaves on weed control and wheat crop productivity. Pak. J. Bot. 2015, 47, 735–740. [Google Scholar]
  64. EMEA/HMPC/137212/2005, Committee on Herbal Medicinal Products (HMPC). Public Statement on the Use of Herbal Medicinal Products Containing Estragole. Available online: http://www.ema.europa.eu/docs/en_GB/document_library/Scientific_guideline/2010/04/WC500089960.pdf (accessed on 20 September 2021).
  65. Dorota, S.; Urszula, K.; Renata, B.; Agnieszka, G. Allelochemicals as Bioherbicides-Present and Perspectives. Herbicides-Current Research and Case Studies in Use; Price, A.J., Kelton, J.A., Eds.; IntechOpen: London, UK, 2013; pp. 517–542. Available online: https://www.intechopen.com/chapters/44466 (accessed on 26 September 2021). [CrossRef] [Green Version]
  66. Belz, R.G.; Hurle, K.; Duke, S.O. Dose-response- A challenge for allelopathy? Nonlinearity Biol. Toxicol. Med. 2005, 3, 173–211. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  67. Li, J.; Inoue, M.; Nishimura, H.; Mizutani, J.; Tsuzuki, E. Interactions of trans-cinnamic acid, its related phenolic allelochemicals, and abscisic acid in seedling growth and seed germination of lettuce. J. Chem. Ecol. 1993, 19, 1775–1787. [Google Scholar] [CrossRef] [PubMed]
  68. Chiapusio, G.; Sánchez, M.A.; Reigosa, J.M.; González, L.; Pellissier, F. Do germination indices adequately reflect allelochemical effects on the germination process? J. Chem. Ecol. 1997, 23, 11. [Google Scholar] [CrossRef]
  69. Wang, W. Literature review on higher plants for toxicity testing. Water Air Soil Poll. 1991, 59, 381–400. [Google Scholar] [CrossRef]
  70. International Organization for Standarization (ISO). Soil Quality-Determination of the Effects of Pollutants on Soil Flora. Part 1. Method for the Measurement of Inhibition of Root Growth; ISO: Geneva, Switzerland, 1993; p. 9. [Google Scholar]
  71. Organization of Economical Cooperation and Development (OECD). Terrestrial Plants, Growth Test; Guideline for Testing of Chemicals 208; OECD: Paris, France, 1984; p. 15. [Google Scholar]
  72. Arango, M.C.; Ringuelet, J.; Viña, S. Intervención de los Compuestos Secundarios en las Interacciones Biológicas. In Productos Naturales Vegetales; Edulp integra la Red de Editoriales Universitarias Nacionales (REUN): Buenos Aires, Argentina, 2013. [Google Scholar]
Figure 1. Effect of different concentrations of Estragole and 2-Isopropylphenol on Allium cepa germination percentage (%GT) and germination rate (%GR), expressed as the percentage relative to the control (Control value: 100%). Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
Figure 1. Effect of different concentrations of Estragole and 2-Isopropylphenol on Allium cepa germination percentage (%GT) and germination rate (%GR), expressed as the percentage relative to the control (Control value: 100%). Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
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Figure 2. Effect of different concentrations of Estragole and 2-Isopropylphenol on Lactuca sativa germination percentage (%GT) and germination rate (%GR), expressed as the percentage relative to the control. Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
Figure 2. Effect of different concentrations of Estragole and 2-Isopropylphenol on Lactuca sativa germination percentage (%GT) and germination rate (%GR), expressed as the percentage relative to the control. Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
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Figure 3. Effect of different concentrations of Estragole and 2-Isopropylphenol on the radicle and hypocotyl length of Allium cepa, expressed as the percentage relative to the control. Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
Figure 3. Effect of different concentrations of Estragole and 2-Isopropylphenol on the radicle and hypocotyl length of Allium cepa, expressed as the percentage relative to the control. Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
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Figure 4. Effect of different concentrations of Estragole and 2-Isopropylphenol on the radicle and hypocotyl length of Lactuca sativa, expressed as the percentage relative to the control. Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
Figure 4. Effect of different concentrations of Estragole and 2-Isopropylphenol on the radicle and hypocotyl length of Lactuca sativa, expressed as the percentage relative to the control. Four replicates of each treatment were performed (n = 4 × 50 = 200 seeds in total for each solution). * Significantly different from the controls. ’ Significantly different from the mixture of compounds. a, b, c: differences in small letters indicate significant differences between concentrations of the same index and for each treatment. p < 0.05 (Mann–Whitney U-test).
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Requesón, E.; Osuna, D.; Santiago, A.d.R.; Sosa, T. Evaluation of the Activity of Estragole and 2-Isopropylphenol, Phenolic Compounds Present in Cistus ladanifer. Agronomy 2022, 12, 1139. https://doi.org/10.3390/agronomy12051139

AMA Style

Requesón E, Osuna D, Santiago AdR, Sosa T. Evaluation of the Activity of Estragole and 2-Isopropylphenol, Phenolic Compounds Present in Cistus ladanifer. Agronomy. 2022; 12(5):1139. https://doi.org/10.3390/agronomy12051139

Chicago/Turabian Style

Requesón, Elena, Dolores Osuna, Ana del Rosario Santiago, and Teresa Sosa. 2022. "Evaluation of the Activity of Estragole and 2-Isopropylphenol, Phenolic Compounds Present in Cistus ladanifer" Agronomy 12, no. 5: 1139. https://doi.org/10.3390/agronomy12051139

APA Style

Requesón, E., Osuna, D., Santiago, A. d. R., & Sosa, T. (2022). Evaluation of the Activity of Estragole and 2-Isopropylphenol, Phenolic Compounds Present in Cistus ladanifer. Agronomy, 12(5), 1139. https://doi.org/10.3390/agronomy12051139

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