Marie Luyckx1, Jean-Francois Hausman2, Stanley Lutts1, Gea Guerriero2. 1. Groupe de Recherche en Physiologie Végétale, Earth and Life Institute - Agronomy, Université Catholique de Louvain Louvain-la-Neuve, Belgium. 2. Environmental Research and Innovation Department, Luxembourg Institute of Science and Technology Esch-sur-Alzette, Luxembourg.
Abstract
Elemental silicon (Si), after oxygen, is the second most abundant element in the earth's crust, which is mainly composed of silicates. Si is not considered essential for plant growth and development, however, increasing evidence in the literature shows that this metalloid is beneficial to plants, especially under stress conditions. Indeed Si alleviates the toxic effects caused by abiotic stresses, e.g., salt stress, drought, heavy metals, to name a few. Biogenic silica is also a deterrent against herbivores. Additionally, Si ameliorates the vigor of plants and improves their resistance to exogenous stresses. The protective role of Si was initially attributed to a physical barrier fortifying the cell wall (e.g., against fungal hyphae penetration), however, several studies have shown that the action of this element on plants is far more complex, as it involves a cross-talk with the cell interior and an effect on plant metabolism. In this study the beneficial role of Si on plants will be discussed, by reviewing the available data in the literature. Emphasis will be given to the protective role of Si during (a)biotic stresses and in this context both priming and the effects of Si on endogenous phytohormones will be discussed. A whole section will be devoted to the use of silica (SiO2) nanoparticles, in the light of the interest that nanotechnology has for agriculture. The paper also discusses the potential technological aspects linked to the use of Si in agriculture and to modify/improve the physical parameters of plant fibers. The study indeed provides perspectives on the use of Si to increase the yield of fiber crops and to improve the thermal stability and tensile strength of natural fibers.
Elementaln class="Chemical">silicon (Si), after oxygen, is the second most abundant element in the earth's crust, which is mainly composed of silicates. Si is not considered essential for plant growth and development, however, increasing evidence in the literature shows that this metalloid is beneficial to plants, especially under stress conditions. Indeed Sialleviates the toxic effects caused by abiotic stresses, e.g., salt stress, drought, heavy metals, to name a few. Biogenic silica is also a deterrent against herbivores. Additionally, Si ameliorates the vigor of plants and improves their resistance to exogenous stresses. The protective role of Si was initially attributed to a physical barrier fortifying the cell wall (e.g., against fungal hyphae penetration), however, several studies have shown that the action of this element on plants is far more complex, as it involves a cross-talk with the cell interior and an effect on plant metabolism. In this study the beneficial role of Si on plants will be discussed, by reviewing the available data in the literature. Emphasis will be given to the protective role of Si during (a)biotic stresses and in this context both priming and the effects of Si on endogenous phytohormones will be discussed. A whole section will be devoted to the use of silica (SiO2) nanoparticles, in the light of the interest that nanotechnology has for agriculture. The paper also discusses the potential technological aspects linked to the use of Si in agriculture and to modify/improve the physical parameters of plant fibers. The study indeed provides perspectives on the use of Si to increase the yield of fiber crops and to improve the thermal stability and tensile strength of natural fibers.
Silicon (n class="Chemical">Si) is considered non-essential (or quasi-essential, Epstein and Bloom, 2005) for plant growth and development. Plants develop well in its absence, although in some cases, e.g., the silicifier horsetail and rice, the absence of Si triggers increased susceptibility to fungal infection (Datnoff and Rodrigues, 2005; Law and Exley, 2011). When supplied to the growth medium (as silicic acid, vide infra), plant vigor and resistance to (a)biotic stresses increase (Azeem etal., 2015; Coskun etal., 2016; Guerriero etal., 2016a). Si is taken up by plants as silicic acidSi(OH)4 via aquaporin type channels (Nod26-like intrinsic proteins, NIPs) (Ma etal., 2006; Grégoire etal., 2012; Deshmukh etal., 2013). A specific 108 amino acid spacing between the conserved NPA domains determines Si(OH)4 permeability (Deshmukh etal., 2015). Plants are classified into accumulators, excluders and intermediate type (Mitani and Ma, 2005), depending on the amount of biogenic silica found in their tissues. Among the accumulators are Equisetales, Cyperales and Poales: in Graminae, rice is the highest silicifier where Si (in the form of biogenic silica, vide infra) accounts for up to 10% of the shoot dry weight (Ma etal., 2002). Tomato is among the excluders, while Urtica dioica (i.e., nettle) is an intermediate type (Trembath-Reichert etal., 2015).
In (some) plants the provision of n class="Chemical">Si(OH)4 has a latent effect in the absence of an external stimulus (Fauteux etal., 2005, 2006). This has been observed in the Arabidopsis-powdery mildew pathosystem (Fauteux etal., 2006). It should, however, be noted that in rice, Si(OH)4 supplementation does trigger major changes, as it induces the upregulation and downregulation of 35 and 121 transcription factors respectively (Van Bockhaven etal., 2012). This difference may be in part due to the different cell wall types (Yokoyama and Nishitani, 2004) and to the structural importance of Si in type II cell walls (i.e., cell walls characterized by the presence of more phenylpropanoids as compared to type I cell walls in dicots).
By precipitating as SiO2 and being incorporated into biologicn class="Chemical">al structures (e.g., the cell wall, vide infra), Si exerts its protective action via the formation of a physical barrier. However, this passive role is too simplistic and does not explain why plants supplemented with Si are better suited to face exogenous stresses. Compelling evidence in the literature shows that specific cell wall components trigger SiO2 precipitation (reviewed by Guerriero etal., 2016a). In rice cell suspension culture, a hemicellulose-bound form of Si has been identified (He etal., 2015), in horsetail mixed-linkage glucans (MLGs) have been proposed to participate in SiO2 formation (Fry etal., 2008) and this has been recently confirmed in rice where overexpression of a hydrolase acting on MLGs was shown to affect silicification (Kido etal., 2015). In horsetail, callose was shown to template biosilicification (Law and Exley, 2011). Very recently, the role of callose in templating biosilicification has been additionally proven by using Arabidopsis plants either overexpressing or lacking the callose synthase gene PMR4 (Brugiére and Exley, 2017): while the wild-type plants and overexpressors responded to a pathogen-like challenge by accumulating both callose and silica, the mutants did not produce callose and, consequently, deposited significantly less silica.
Si Priming
Several papers demonstrated that n class="Chemical">Si(OH)4 (hereafter referred to as Si for simplicity) acts as a “tonic” by priming plants, i.e., by preparing the defense responses which are then fully deployed at the onset of the stress, as will be discussed in detail in the next sections. The effects of Si under normal conditions are indeed latent, since, for the majority of the studies available, no major modifications, e.g., in gene expression, are observed. Under control conditions Si probably activates the metabolic status of the plant, by making it more efficient in responding to exogenous stimuli.
In rice, a n class="Chemical">Si-accumulator, Si causes alterations of C/N balance in the source-sink relationship under unstressed conditions, by favoring a remobilization of amino acids to support the increased N demand during grain development (Detmannetal., 2012, 2013). These data support the hypothesis that Si has a signaling role in plant cells. Si was indeed suggested to have a role as second messenger by binding to the hydroxyl groups of proteins involved in cell signaling, thereby partaking in the signal transduction (Fauteux etal., 2005).
It is important to mention that Si primes defense responses n class="Chemical">also in Si non-accumulators, i.e., tomato (Ghareeb etal., 2011): tomato is protected against Ralstonia solanacearum by Si which causes an upregulation, upon infection, of genes involved in ethylene and jasmonic acidsignaling, i.e., JERF3, TRSF1, ACCO, as well as genes involved in stress response, i.e., trehalose phosphatase, late embryogenesis abundant protein, ferritin. In this study, the authors also observed an increased expression of a negative regulator of the jasmonic acidsignal, JAZ1, together with a ubiquitin protein-ligase: the authors propose that JAZ1 helps in preventing the eventual damage caused by the stimulation of defense-related compounds and that the ubiquitin protein-ligase may degrade JAZ1. In tomato challenged by R. solanacearum, Sialso upregulates a MAPK (MAPK19), a WRKY transcription factor and linker histones (H1 and H5). These findings corroborate the role of Si in intracellular signaling and suggest its involvement in transcription too (Ghareeb etal., 2011).
Silicon was shown to upregulate the expresn class="Chemical">sion of a leucine-rich repeat receptor-like kinase (LRR-RLK) in rice (Fleck etal., 2011), which is a protein involved in intracellular signal transduction. High-throughput technologies relying on –omics will help shed light on the missing genes/proteins involved in the signal transduction underlying Si priming (the so-called “prime-omics”; Balmer etal., 2015).
Si and Abiotic Stress Alleviation
Si assumes key functions in the plant response to numerous environmentn class="Chemical">al constraints. Two major processes contributing to stress resistance are commonly considered (i) a physical and mechanical protection afforded by SiO2 deposits and (ii) a biochemical response triggering metabolic changes. The precise distribution/speciation of accumulated Si in plant tissue allows us to gain additional information regarding its modalities of action and requires the use of biophysical tools, such as laser ablation (LA), extended X-ray fine structure (EXAFS), X-ray absorption near edge structure (XANES) and micro particle-induced X-ray emission (micro-PIXE).
According to Liang etn class="Chemical">al. (2013), Si improves lodging resistance by strengthening the stem basis in rice. It also enhances UV tolerance due to the protective effect of Si deposition bodies on the leaf epidermis (Goto etal., 2003) or by reducing UVB-induced membrane damages (Shen etal., 2010).
Silicon influences n class="Chemical">water relations in drought-treated plants: it induces the formation of a silicacuticle double layer under the leaf epidermis which reduces water losses through cuticular transpiration (Gong etal., 2003). Sialso reduces stomatal conductance in relation to turgor loss of guard cells resulting from Si deposition and modified cell wall properties (Zhu and Gong, 2014). Si improvement of drought resistance may also be ascribed to strong abilities to extract water from the soil as a consequence of Si-related promotion of root elongation (Hattori etal., 2005) and up-regulation of aquaporin genes (Liu etal., 2015).
Silicon contributes to n class="Chemical">salt stress alleviation through inhibition of Na+ (Zhu and Gong, 2014) and Cl- (Shi etal., 2013) uptake. Translocation of toxic ions from root to shoot is also reduced by Si supply (Savvas and Ntatsi, 2015). In rice, Sialleviates NaCltoxicity by blocking the transpirational bypass flow through precipitation as SiO2 in exodermis and endodermis (Yeo etal., 1999). Potassium uptake allowing the maintenance of K/Na is improved by Si nutrition which has a direct stabilizing effect on proton pump activity in salt-treated root tips (Xu etal., 2015).
In metal-polluted soil, n class="Chemical">Si may influence the bioavailability of toxic elements. The presence of soil sodium metasilicate or alkaline Si-containing material may induce a rise in the rhizospheric pH leading to a decrease in available heavy metal concentration in the soil (Wu etal., 2013). Soluble silicate hydrolyzes to generate gelatinous metasilicic acid (H2SiO3) retaining heavy metals (Gu etal., 2011). According to Kidd etal. (2001), Si-treated plants may also exude phenolics such as catechin and quercetin having strong Al-chelating abilities. The formation of hydroxyl-aluminum silicate in the apoplast also contributes to Al detoxification (Wang etal., 2004).
Compartmentation of toxic ions is an important process in heavy metal tolerance. n class="Chemical">Si improves heavy metal retention by roots, with an obvious accumulation in the endodermis (Keller etal., 2015). At the shoot level, accumulation of Mn was mainly observed in epidermis in response to Si treatment (Doncheva etal., 2009). Iwasaki and Matsumura (1999) reported that Si increases Mn accumulation in the leaf trichomes. Controversial data are available in the literature regarding co-precipitation of Si with heavy metals. Keller etal. (2015) did not detect Cu and Cd in phytoliths and the absence of Cu-Si coprecipitation was also noticed in maize by Collin etal. (2014). He etal. (2013), however, identified a mechanisms of co-deposition of Si and Cd in the rice cell walls via a [Si-wall matrix] Cd complexation, which may explain a Si-induced decrease in the Cd influx in cells. Ma etal. (2015) considered that a hemicellulose bound form of Si with a net negative charge is responsible for inhibition of Cd uptake leading to a downregulation of Nramp5 coding for a transporter involved in Cd transport. Kim etal. (2014) also reported a downregulation of other heavy metals transporter (OsHMA2 and OsHMA3) when Cu/Cd-treated rice was supplied by Si.
Numerous studies reported that Si induces an improved behavior of heavy n class="Chemical">metal-treated plants in relation to regulation of antioxidant enzymes (Adrees etal., 2015), oversynthesis of endogenous antioxidants leading to mitigation of oxidative stress (Imtiaz etal., 2016), maintenance of net photosynthesis relying on the stabilization of chloroplast structures, PSII integrity and increased pigment concentration (Nwugo and Huerta, 2008; Tripathi etal., 2015a). Si may thus be of paramount importance for triggering adapted plant response, but the precise molecular cues involved in the adaptative processes still need to be clearly identified.
Si and Biotic Stress
Si was reported to improve defense against biotic constraints ocn class="Chemical">curring in the form of plant pathogens (fungi, bacteria, and viruses) or animals (vertebrates and arthropod herbivores).
Silicon depon class="Chemical">sition increases abrasiveness of plant tissues and thus reduces palatability and digestibility for herbivores (Massey and Hartley, 2009). Hartley etal. (2015) demonstrated by Scanning electron microscopy with energy dispersive X-ray spectroscopy (SEM-EDX) that phytolith morphology inside the tissues has more influence on abrasiveness than the actualSi concentration. Using the same technique, Keeping etal. (2009) demonstrated that the pattern of Si deposition in sugarcane is responsible for enhanced resistance to Eldana saccharina. Physical strength of the leaf resulting from Si accumulation may afford mechanical protection and thus lower the rate of infection as reported for Rhizoctonia solani (Zhang etal., 2013; Schurt etal., 2014) or Bipolaris oryzae (Ning etal., 2014).
Biochemical/molen class="Chemical">cular mechanisms are also induced or re-inforced by Siallowing the plant to improve resistance to biotic stress and include defensive compounds such as phenolics, phytoalexins and momilactones (Remus-Borel etal., 2005), but also to activation of defensive enzymes such as peroxidase, polyphenol oxidase, lipoxygenase and phenylalanine ammonia lyase (Rahman etal., 2015). According to Cai etal. (2008), Si treatments may increase transcripts levels corresponding to those defense-related genes.
Reynolds etn class="Chemical">al. (2016) reported that Sialso operates by attracting predators or parasitoids to plant under herbivore attack. Indeed, soluble Si contributes to increase herbivore-induced plant volatiles to promote predator attraction by pest-infected plants. Moreover, according to James (2003) and Connick (2011), the phenology of insect’s life cycle is also slowed down in Si-treated plants, making it more prone to predation.
Effects of Si on Phytohormones
Silicon impacts on endogenous phytohormones are commonly ann class="Chemical">alyzed in response to stress conditions. In rice plants exposed to heavy metals, Si reduced endogenous concentration of jamonic acid (JA) and salicylic acid (SA), while abscisic acid (ABA) first increased and then decreased after 14 days of treatment (Kim etal., 2014): the ABA has an antagonist behavior with JA/SA biosynthesis. The effect of such phytohormonal changes on the expression of genes involved in heavy metal response still needs to be elucidated in Si-treated plants. Kim etal. (2011) also reported that Si reduced JA concentration in response to wounding, while Lee etal. (2010) reported an increase in gibberellins concentration in Si-treated plants exposed to salinity.
Resistance to biotrophic pathogens may be associated with n class="Chemical">SA whereas JA and ethylene (ET) are generally associated with resistance to necrotrophic pathogens. Fauteux etal. (2006) showed that Si improved biosynthesis of SA, JA and ET in leaves exposed to Erysiphe cichoracearum. Similarly, Si-treated tomato plants exposed to R. solanacearum activated JA and ETsignaling pathways to increase resistance (Ghareeb etal., 2011). Brunings etal. (2009) also provided evidence that genes controlling ETsignaling pathway may be activated by Si treatment. Conversely, Si improves resistance to the fungus Cochliobolus miyabeanus by interfering with the production of fungalET (Van Bockhaven etal., 2015). Data regarding the effect of Si on phytohormone metabolism in the absence of stress are still rare. Markovich etal. (2017), however, recently demonstrated that Si increases cytokinin biosynthesis in Sorghum and Arabidopsis and that such an increase may strongly contribute to delay senescence. Plant hormones interactions are responsible for a complex biochemical and physiologicalnetwork: a deep understanding of Si influence on hormonal properties thus requires technical approaches allowing to quantify a wide range of hormonal compounds simultaneously, including minor conjugated forms.
Silica Nanoparticles
The use of nanotechnology in agriculture is gaining importance because it contributes to develop new sustainable strategies. Nanomaterin class="Chemical">als can for example be engineered to immobilize nutrients or to release them in a controlled manner in the soil (Fraceto etal., 2016).
Some papers in the literature have studied the effects of silicananoparticles (SNPs) on plant physiology and we will here review some of them.Mesoporous SNPs (MSNPs, 20 nm in n class="Chemical">size) coupled to FITC were shown to be taken up by three important crops (lupin, wheat, maize), as well as Arabidopsis protoplasts and to be translocated to the aerial parts following the xylematic flow after entering the roots via symplastic/apoplastic routes (Sun etal., 2014). Very interestingly, this study also showed that MSNPs accumulated in the cell walls, therefore highlighting the existence of an affinity with cell wall components. The monodisperse nature of the MSNPs and their size, achieved via a fine-tuning of pH and surfactant concentration, were essential for the efficient uptake by plants: the entry takes place via the pores in the cell walls of the roots cells (Sun etal., 2014).
Mesoporous SNPs were shown to boost the growth, totn class="Chemical">al protein content and photosynthesis of lupin and wheat seedlings and to induce no changes in the activity of antioxidant enzymes (Sun etal., 2016). Interestingly in this study, the authors observed a shift of 14 cm-1 and 10 cm-1 in the Raman peaks of chlorophyll from wheat and lupin when isolated chloroplasts were incubated with MSNPs suggesting a change in the molecular structure of chlorophyll.
Silicananoparticles were shown to protect n class="Species">wheat seedlings against UV-B stress by stimulating the antioxidant defense system (Tripathi etal., 2016). In particular, SNPs reduced the adverse effects of the UV-B stress, i.e., low fresh weight, reduction in chlorophyll and tissue damage. Since the levels of nitric oxide reached a peak after UV-B+SNPs treatment, a protective role via the modulation of NO levels was proposed by the authors.
Silicananoparticles n class="Chemical">also conferred protection via mitigation of oxidative stress in pea seedlings treated with Cr(VI): the activities of enzymes such as superoxide dismutase, ascorbate peroxidase increased significantly in the presence of SNPs, while catalase, glutathione reductase and dehydroascorbate reductase were less inhibited by Cr(VI) in the presence of SNPs (Tripathi etal., 2015b).
Silicananoparticles (12 nm) were n class="Chemical">also found to improve germination in a known Si-excluder, tomato: at a concentration of 8 g/L, SNPs improved seedling germination, as well as fresh and dry weight by 116.6 and 117.5% respectively (Siddiqui and Al-Whaibi, 2014).
Nanostructured SiO2 (TMS) was shown to be valuable in larch seedling production, because, when applied to the roots of 1-year-old seedlings via soaking for 6 h, it promoted lateral root growth, main root length and chlorophyll content (Bao-shan etal., 2004).The effect of SNPs was, however, shown to be dependent on the plant species, as in Bt-transgenic cotton they significantly den class="Chemical">creased plant growth (Le etal., 2014). SNPs toxicity may be linked to pH and nutrient adsorption problems. Indeed, in thale cress, SNPs phytotoxicity was triggered when the pH of the medium was not adjusted or silanol groups were not removed from the surface (Slomberg and Schoenfisch, 2012). The alkaline pH (pH 8 ca.) makes nutrients less available for uptake, while the negatively charged SNPs tend to adsorb nutrients.
Si and Fiber Crops
Fiber crops like textile n class="Species">hemp (Cannabis sativa L.) are natural resources which provide long and strong cellulosic fibers (a.k.a. bast fibers) used in both the textile and biocomposite sectors (Guerriero etal., 2014; Andre etal., 2016; Guerriero etal., 2016b). Given the positive effects of Si on plants, its use for fiber crop growth may provide an enhanced biomass yield and, therefore, an increased production of bast fibers. The association of SiO2 with the fiber cell walls may provide new properties, notably and increased durability. In this respect, it should be noted that hemp woody fibers, which contain SiO2 and therefore bind well with lime, are already used to manufacture a lightweight concrete-like material used in eco-construction and known as hempcrete. The few studies available on the specific Si impact on fiber crops confirm protection against abiotic stresses. In ramie [Boehmeria nivea (L.) Gaud.], the application of Si ameliorated Cdtoxicity via stimulating the activities of antioxidant enzymes (Tang etal., 2015). Bakry etal. (2015) and Shedeed etal. (2016) reported that foliar application of Si improved the nutrient status of flax and increased straw and oil yield/plant.
Silicon acn class="Chemical">cumulation in fiber crops is genetically controlled, as demonstrated for bamboos by Collin etal. (2012). Exogenous Si did not reduce Cu absorption by bamboos growing on contaminated solution, but reduced toxicity symptoms (Collin etal., 2013, 2014). Sialso improved the growth of cotton exposed to Cd but, in this case, Si reduced Cd uptake and mitigated the adverse effect of this heavy metal by improving plant growth, biomass and photosynthetic parameters in stressed plants (Farooq etal., 2013).
Data concerning the direct influence of Si on fiber development itself are n class="Chemical">crucially lacking. Some old studies, however, provided indirect evidences that Si may assume important functions in this respect. Khan and Roy (1964) reported that soil application of silicate improved the size of the commercial fiber jute by increasing cell elongation and fineness. According to Boylston (1988), the Si concentration is high during the elongation phase of cotton fiber development but decreases as the fiber matures. The ratio of the amount of Si per mass of fiber peaks at the time when secondary wall initiation occurs (Boylston etal., 1990). Si is known to interact with cell walls (see Introduction), although the mechanisms underlying the final incorporation of polymerized Si into the cell wall remain elusive. Kido etal. (2015) recently demonstrated that the interaction of mixed linkage glucan (1;3, 1;4)-β-D-glucan with Si may have obvious mechanical consequences.
Si beneficin class="Chemical">al influence on natural fiber properties is confirmed by the use of Si-containing compounds during industrial processing of harvested fibers. Natural fibers are gaining attention in engineering composite industry. However, cell wall polymers often bear hydrophilic hydroxyl groups able to form new hydrogen bonds with water molecules, which hinder hydroxyl group to react with the polar matrix of the composites (Mwaikambo and Ansell, 2002). Silane is an inorganic compound (SiH4) commonly used to improve tensile strength and thermal stability of natural fibers (Abdelmouleh etal., 2004) which may be due to the emergence of Si-O-C and Si-O-Si links on the cellulose surface (Lu etal., 2013). Other Si treatment, including siloxane and nano Si dioxide are also used for similar purposes (Kabir etal., 2012; Siengchin and Dangtungee, 2014; Orue etal., 2016). It may thus be hypothesized that Si treatment in vivo during fiber development (and not only in vitro on harvested mature fibers) may lead to several promising application. This exciting goal, however, requires a multidisciplinary approach to gain a better understanding of Si influence on the modalities of fiber development (Figure ).
Global overview of n class="Chemical">Si impact on hemp (. Speciation of Si in soil and application of SiO2 nanoparticles are indicated in brown boxes and possible sites of Si deposit in the plant are indicated in green boxes. Resulting consequences of Si accumulation in terms of stress resistance and underlying physiological processes are indicated in blue boxes. For further details, please refer to the text. A deep understanding of processes involved in Si absorption, translocation and physiological consequences require holistic -omics approaches including transcriptomics, proteomics and metabolomics tools. The precise Si distribution may be assessed by laser ablation (LA), extended X-ray fine structure (EXAFS), X-ray absorption near edge structure (XANES) and micro particle-induced X ray emission (micro-PIXE).
Conclusion and Future Perspectives
Silicon is an abundant element on Earth and its pon class="Chemical">sitive effects on plants make it important in agriculture. The study of the Si-plant binomium has still much to teach us and this is particularly the case for e.g., the cell wall-related mechanisms underlying its prophylactic role under stress. The plant cell wall takes active part in the response to (a)biotic stresses by establishing a signaling cascade toward the cell interior (Hamann, 2015) and by undergoing a remodeling (Tenhaken, 2014). It is therefore clear that part of the beneficial effects of Si on plants is linked to direct/indirect effects on the cell wall.
In the future, research activities centered on specific aspects of the interaction Si-plants will be important to devise agrin class="Chemical">cultural strategies aimed at improving crop yield.
Author Contributions
GG conceived the idea of writing the paper. ML, J-FH, SL, and GG collected the literature data and wrote the manuscript.
Conflict of Interest Statement
The authors declare that the research was conducted in the absence of any commercial or financin class="Chemical">al relationships that could be construed as a potential conflict of interest.
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