C H A P T E R
9 Role and Regulation of Plants Phenolics in Abiotic Stress Tolerance: An Overview Mohd Irfan Naikoo1, Mudasir Irfan Dar1, Fariha Raghib1, Hassan Jaleel2, Bilal Ahmad2, Aamir Raina3,4, Fareed Ahmad Khan1 and Fauzia Naushin3 1
Plant Ecology and Environment Laboratory, Department of Botany, Aligarh Muslim University, Aligarh, Uttar Pradesh, India 2Plant Physiology Laboratory, Department of Botany, Aligarh Muslim University, Aligarh, Uttar Pradesh, India 3Botany Section, Women’s College, Aligarh Muslim University, Aligarh, Uttar Pradesh, India 4 Mutation Breeding Laboratory, Department of Botany, Aligarh Muslim University, Aligarh, Uttar Pradesh, India
O U T L I N E 9.1 Introduction
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9.2 Structure and Classification
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9.3 Biosynthesis of Polyphenols
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9.4 Phenolics and Abiotic Stress Tolerance 158 9.4.1 Phenolics as Ultraviolet Sunscreens 161 9.4.2 Plant Phenolics and Their Role in Heavy Metal Stress 162 9.4.3 Plant Phenolics and Their Role in Drought Stress 163
9.1 INTRODUCTION Plants are exposed to multifarious abiotic stresses in constantly changing environments that are unfavorable for growth and development (Zhu, 2016). These abiotic stresses include water (drought and flooding), heavy metals, salinity, excess or deficiency of nutrients, high and low temperatures (chilling and freezing), extreme levels of light (high and low), radiation
Plant Signaling Molecules. DOI: https://doi.org/10.1016/B978-0-12-816451-8.00009-5
9.4.4 Plant Phenolics and Their Role in Cold Stress 163 9.4.5 Plant Phenolics and Their Role in Nutrient Stress 163 9.5 Conclusion and Future Prospects
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References
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Further Reading
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(UV-B and UV-A; ultraviolet, UV), ozone, sulfur dioxide, mechanical factors, and other less frequently occurring stressors (Pereira, 2016). Plants being rooted in the environment they grow in have to adapt with the changing conditions due to abiotic stresses and the accumulation of phenolics in plant tissues are considered as an adaptive response of plants to these adverse environmental conditions (Pereira, 2016; Lattanzio, 2013).
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© 2019 Elsevier Inc. All rights reserved.
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9. ROLE AND REGULATION OF PLANTS PHENOLICS IN ABIOTIC STRESS TOLERANCE: AN OVERVIEW
Plants synthesize an enormous number of chemicals categorized as primary and secondary metabolites. The primary metabolites, that is, sugars, fatty acids, amino, and nucleic acids being essential for plant growth and development are ubiquitously distributed in all plants (Fiehn, 2002; Wu and Chappell, 2008). Secondary metabolites being much more diverse than the primary metabolites structurally as well as chemically are the specialized compounds that are not directly essential for basic plant metabolism but are required by plants for survival in the environment. Plant phenolics or polyphenols are the most widely occurring groups of secondary metabolites with substantial physiological and morphological importance in plants. They are aromatic compounds with one or more hydroxyl groups and emerge from shikimate/ phenylpropanoid pathway or polyketide acetate/malonate pathway, producing monomeric and polymeric phenols and polyphenols (Randhir et al., 2004). Plant phenolics play an important role in plant growth, development, and reproduction, and a key role as defense compounds against abiotic stresses, such as high light, low temperatures, UV-B radiations, heavy metals and nutrient deficiency (Lattanzio, 2013), protection against pathogens and predators (Bravo, 1998), producing color and sensory characteristics of fruits and vegetables (Alasalvar et al., 2001), besides exhibiting other essential properties like antiallergenic, antimicrobial, and antioxidant activity (Balasundram et al., 2006). Plant phenolics or polyphenols are the most widely distributed secondary metabolites and predominate in the plant kingdom. Bacteria, fungi, and algae produce peculiar phenolic compounds whereas bryophytes are regular producers of polyphenols like flavonoids, but in the vascular plants a full range of phenolic compounds or polyphenols are found (Swain, 1975; Harborne, 1980). An estimation of about 2% of all the carbon photosynthesized by plants is converted into phenolic compounds (Robards and Antolovich, 1997). Several thousand phenolic compounds are known to be synthesized by higher plants and the characterization of these compounds is continuously increasing. Plant leaves contain esters; amides and glycosides of hydroxycinnamic acids (HCAs); glycosylated flavonoids, particularly flavonols; and proanthocyanidins and their derivatives. Lignin, suberin, and pollen sporopollenin are some other polyphenolic polymers. Some soluble phenolics like chlorogenic acid are widely distributed, whereas some are restricted to specific genera or families, thereby are handy biomarkers for taxonomic studies.
9.2 STRUCTURE AND CLASSIFICATION Structurally, phenolic compounds contain an aromatic ring with one or more hydroxyl substituents
attached to it, ranging from simple phenolic molecules to highly polymerized compounds, thereby showing great structural diversity, and are often referred to as polyphenols (Bravo, 1998). Most phenolic compounds naturally appear as conjugates with mono- and polysaccharides, coupled with one or more phenolic groups, and may also exist as functional derivatives like esters and methyl esters (Harborne, 1989; Harborne et al., 1999; Shahidi and Naczk, 1995). Phenolics though a very large and diverse group of chemical compounds can be classified in a number of ways. Harborne and Simmonds (1964) classified them into different groups based on the number of carbons in the molecule (Table 9.1).
9.3 BIOSYNTHESIS OF POLYPHENOLS Plant phenolics are biosynthesized in plants from a biosynthetic intermediate, phenylalanine and shikimic acid through the shikimic acid pathway (Fig. 9.1). The starting metabolites of the pathway are erythose-4phosphate and phosphoenolpyruvate (PEP), which are intermediates of pentose phosphate pathway (PPP) and glycolysis, respectively. The first step involves the conversion of glucose in the PPP to glucose-6-phosphate and then irreversibly to ribulose-5-phosphate by the aid of glucose-6-phosphate dehydrogenase (G6PDH). The PPP advances to produce erythrose-4-phosphate. Similarly from glycolysis, phosphoenolpyruvate is generated, which is then used together with erythrose-4-phosphate through the phenylpropanoid pathway to generate phenolic compounds after being channeled to the shikimic acid pathway to produce phenylalanine (Fig. 9.1).
9.4 PHENOLICS AND ABIOTIC STRESS TOLERANCE The great degree of interactions between plants and their changing environments has been a major driving force behind the emergence of specific natural products (Lattanzio, 2013). In this regard, the accumulation of phenolics in plant tissues is considered as an adaptive response of plants to adverse environmental conditions, thereby expanding evolutionary fitness. This accumulation resulted due to the activity of phenylalanine ammonia lyase (PAL), chalcone synthase (CHS), and other enzymes. Activity of PEPcarboxylase also increases, indicating a shift from sucrose production to the processes of defense and repair. Plant phenolics confer various physiological functions for survival and adaptation to environmental disturbances (Landolt et al., 1997; Andersen, 2003;
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TABLE 9.1 Classification of Phenolic Compounds Class
No. of C-atoms
Structure
Occurrence
Simple phenolics, benzoquinones
6
C6
Rare to common
Phenolic acids and related compounds
7
C6 C1
Common
Acethophenones, phenylacetic acids
8
C6 C2
Rare
HCAs, phenylpropanoids (coumarins, isocoumarins, chromones, chromenes)
9
C6 C3
Rare to common
Napthoquinones
10
C6 C4
Xanthones
13
C6 C1 C6
Rare
Stilbenes, anthraquinones
14
C6 C2 C6
Rare
Flavonoids, isoflavonoids
15
C6 C2 C6
Common
Betacyanins
18
Lignans, neolignans
18
(C6 C3)2
Biflavonoids
30
(C6 C3 C6)2
Rare
(C6 C3)n
Common
Lignin Melanins Condensed tannins (proanthocyanidins flavolans)
N
Rare
(C6)n (C6 C3 C6)n
FIGURE 9.1 The phenolic compound biosynthesis pathway. A schematic representation of the biosynthesis of phenolic compounds in the pentose phosphate, shikimate, and phenylpropanoid pathways in plants. Source: Redrawn from Lattanzio, V., 2013. Phenolic compounds: introduction. In: Ramawat, K.G., Merillon, J.M. (Eds.), Natural Products, Springer-Verlag: Berlin, Heidelberg. http://doi.org/10.1007/978-3-642-22144-6_57 and Lin et al. (2016).
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Lattanzio et al., 2009). Plant phenolics are generally considered pivotal defense compounds when environmental stresses, such as high light or UV radiation, low temperatures, pathogen infection, herbivores, heavy metals, and nutrient deficiency, lead to increased production of free radicals and other oxidative species in plants. Plants respond to these biotic and abiotic stress factors by increasing their capacity to scavenge reactive oxygen species (ROS; Khan and Khan, 2017). The induction of secondary metabolism gene expression by the abovementioned environmental stresses is often mediated by integrating signaling molecules such as salicylic acid, jasmonic acid, and their derivatives (WinkelShirley, 2002; Gould and Lister, 2006; Nascimento and Fett-Neto, 2010; Khan and Khan, 2013; Khan et al., 2013, 2014, 2015; Per et al., 2018). Plants are exposed to various abiotic stresses during their life cycle. When a plant is subjected to abiotic stress, a number of genes are turned on or off, resulting in increasing levels of several metabolites and proteins, some of which may be responsible for conferring a certain degree of defense against these stresses (Ahmad et al., 2008; Jaleel et al., 2009; Tuteja et al., 2009). Abiotic stress promotes the production of damaging active oxygen species within the cells (Dar et al., 2017). Phenolics are varied secondary metabolites (flavonoids, tannins, hydroxycinnamate esters, and lignin) found abundantly in plant tissues and are actively involved in defense mechanisms against biotic and abiotic stress. As compared with nonstressed conditions, plants often produce a higher quantity of phenolic compounds under certain stress conditions (Selmar, 2008). Phenolic compounds performing as antioxidants terminate free radical chains and chelate redox-active metal ions that are capable of catalyzing lipid peroxidation (Schroeter et al., 2002). Phytophenolics, particularly polyphenols, function as antioxidants to support the primary ascorbatedependent detoxification system as a backup defense mechanism of vascular plants contrasting to monophenols (Yamasaki et al., 1995, 1999). Polyphenols are more effective antioxidants in vitro than ascorbate and tocopherols and have an ideal structural chemistry for free radical-scavenging activity. Antioxidative features of polyphenols arise from the ability of the polyphenol-derived radical to steady and delocalize the unpaired electron (chain-breaking function), their high reactivity as hydrogen or electron donors and from their capability to chelate transition metal ions (termination of the Fenton reaction) (Rice-Evans et al., 1997). Kagan and Tyurina (1997) reported that phenolics are univalently oxidized to their respective phenoxyl radicals when they function as antioxidants either by enzymatic or direct radical-scavenging
mechanisms. Plants synthesize phenolic compounds to survive in stress conditions (UV radiation, drought, salt, metal, and low temperature stress). Most plants constitutively synthesize phenylpropanoids including flavonoids and HCAs. However, accumulation of phenolics in plants can be induced by abiotic and biotic stresses, for example, UV radiation, high light illumination, low temperatures, wounding, low nutrients, and pathogen attack (Dixon and Paiva, 1995; Yamasaki et al., 1995). Certain secondary metabolic compounds are intensively synthesized under conditions of abiotic stress like drought where these act as antioxidants (Nascimento and Fett-Neto, 2010). Phenolic compounds accumulation in plant tissues is regarded as a distinctive plant stress characteristic. One among the largest three groups of secondary metabolites produced in plants, phenols have been alienated into five subgroups (coumarins, flavonoids, lignins, phenolic acids, and tannins) (Gumul et al., 2007), and are synthesized in plants via shikimic acid and chorismic acid pathways. Phenolic compounds have been regarded as metabolic alteration byproducts (Solecka, 1997). These not only serve a vital function of defense in plants but are also known to influence animals and humans that consume these phenol-enriched plant products (Franca et al., 2001; Amarowicz and Weidner, 2009). The expression of phenolic compounds has been, however, observed to be upregulated (Wro´bel et al., 2005; Weidner et al., 2009a) or downregulated (Weidner et al., 2007, 2009b) in response to diverse environmental stresses, thus leading to the increased or decreased content of the phenolic compounds. A number of studies have demonstrated the increased production of phenols in different plant tissues under abiotic stress conditions (Dixon and Paiva, 1995; Wro´bel et al., 2005; Weidner et al., 2009a). During water deficit and chilling stress conditions, Chung et al. (2006) have reported increased content of total phenolic compounds in Rehmannia glutinosa. Further confirmation has come from the studies of Posmyk et al. (2005) in soybean subjected to chilling stress. This accumulation is due to enhanced activities of enzymes, PAL, CHS, and other enzymes involved in their biosynthesis. Additionally, phosphoenolpyruvate (PEP)-carboxylase activity also increases, which suggests a shift from the production of sucrose to metabolic processes supporting defense and repair. Phenolics confer a variety of physiological functions to plants to survive and adapt to various environmental disturbances (Landolt et al., 1997; Andersen, 2003; Lattanzio et al., 2009). Phenolic acids are synthesized in response to abiotic stress through hydration, dehydration, and methylation of cinnamic acid (Dixon and Paiva, 1995). Many
PLANT SIGNALING MOLECULES
9.4 PHENOLICS AND ABIOTIC STRESS TOLERANCE
secondary metabolism products in plants that exhibit antioxidant properties belong to this class of compounds (Oszmanski, 1995). As antioxidants, these phenolic compounds scavenge ROS (Amarowicz et al., 2004, 2010; Caillet et al., 2006; Amarowicz and Weidner, 2009), catalyze oxygenation reactions by forming complexes with some metals, and hinder the activities of certain oxidizing enzymes (Elavarthi and Martin, 2010). As stated earlier, accumulation of phenols in plant tissues is a characteristic feature of several environmental stresses that divert considerable quantity of substrates from primary metabolism to the formation of secondary products leading to significant perturbations in the cellular homeostasis. Strong stimulation of mRNAs encoding G6PDH, a carbohydrate metabolism enzyme that provides shikimate pathway substrates, and 3-deoxyarabinoheptulosonate 7-phosphate synthase, which is a shikimate pathway enzyme required for phenylalanine biosynthesis has been observed in response to stress (Cheynier et al., 2013). Furthermore, accumulation of free proline in plants as a result of various biotic and abiotic stresses has been reported. Researchers have anticipated that a stress-stimulated enhancement in the shift of reducing equivalents into proline biosynthesis (cytosolic) as well as degradation (mitochondrial) cycle might be responsible for enabling sensitive regulation of redox potential in the cytosol (Logemann et al., 2000; Lattanzio et al., 2009; Verslues and Sharma, 2010). The abovementioned points imply that different environmental perturbations selectively induce the primary as well as secondary metabolic activities, which are directly and indirectly involved in the accretion of phenolic compounds (Cheynier et al., 2013; Lattanzio et al., 2009). A likely series of biochemical reactions occurring inside the cell, which convey a signal from the outside cell environment into the inside of the plant cell, leading to an effective physiological response, may thus be envisaged (Fig. 9.2) (Hare and Cress, 1997; Lattanzio et al., 2009). This signaling pathway proposes a connection between primary and secondary metabolism, which couples the accretion of proline (a stress metabolite) with the energy transfer toward the biosynthesis of phenylpropanoid through the oxidative PPP (Cheynier et al., 2013). Under various stress conditions, the plant undergoes forceful accumulation of ample amounts of free proline. It can be synthesized de novo or can be released by the protein degradation and is accompanied by NADPH oxidation. Enhanced NADP1/NADPH ratio leads to increased activity of the oxidative PPP, which in turn provides precursors for biosynthesis of phenolic compounds via the shikimic acid pathway (Cheynier et al., 2013; Lattanzio et al., 2009).
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FIGURE 9.2 Showing the abiotic stress-mediated phenol biosynthesis in plants. Source: Redrawn from Cheynier et al. (2013); Lattanzio V., Cardinali, A., Ruta, C., Morone Fortunato, I., Lattanzio, V.M.T., Linsalata, V., et al., 2009. Relationship of secondary metabolism to growth in oregano (Origanum vulgare L.) shoot cultures under nutritional stress. Environ. Exp. Bot. 65, 54 62.
9.4.1 Phenolics as Ultraviolet Sunscreens Light is a well-known physical factor that can affect the synthesis of metabolites in plants. Exposure of ambient solar UV-B radiation (280 320 nm) to plants in open fields adversely affects DNA, proteins, and membranes and alters metabolism through the generation of ROS. Plants synthesize phenolic compounds, which act as a screen inside the epidermal cell layer to defend themselves from this damaging radiation and by adjusting the antioxidant systems at both the cell and whole organism level thereby intercepting mutagenesis and cell death by dimerization of thymine units in the DNA, and possible photo destruction of coenzymes NAD or NADP (Daayf and Lattanzio, 2008). Flavonoids with their high absorptivity at 250 270 and 335 360 nm act as good UV screens (Lattanzio, 2013; Winkel-Shirley, 2002; Carletti et al., 2003). Flavonoids and other phenolic compounds play a significant role in UV protection (Li et al., 1993). Increased flavonoid synthesis was observed in plants radiated with UV light, which confirms the ability of flavonoids to absorb radiation of high energy with the maximum absorption at 250 270 and 335 360 nm (Michalak, 2006; Falcone Ferreyra et al., 2012; Winkel-Shirley, 2002; Liang et al., 2006). It is an observed fact that tropical and high-altitude plants have a higher percentage of flavonoids than temperate plants. The change in the
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proportion of flavonoids composition of plant leaves is due to excess of light or UV radiation largely due the activation of flavonoid biosynthetic genes (Kolb et al., 2001). Several studies have confirmed that the excess of light or UV radiation changes the flavonoid composition of plant leaves (Olsson et al., 1998; Kolb et al., 2001). Plant defense mechanisms of polyphenols against UV radiation as direct shields has been regarded as a key biological function by several authors (Rozema et al., 2002; Burchard et al., 2000). Larcher (1995) revealed that phenolics, particularly anthocyanin, which accumulate in the epidermis can act as a darkening filter and protect the mesophyll from extreme radiation. Flavonoids (especially kaempferol derivatives), phenolic acid esters, or isoflavonoids and psoralens accumulate during stress and prevent UV-B from reaching the mesophyll (Stapleton, 1992). Flavones and flavonols, the two important groups of flavonoids found in flowers, accumulate in epidermal layers of leaves and stems and absorb light strongly in the UV-B region without interrupting visible (PAR) wavelengths, thus function to shield cells from UV-B radiation (Lake et al., 2009). Ryan et al. (2001) proved that flavonoids are essential in UV protection using mutants of Arabidopsis, UV-hypersensitive phenotypes that have a block in flavonoid production. Anthocyanin synthesis was stimulated by UV light from 280 to 320 nm synergistically when combined with red light in apples (Arakawa et al., 1985). Liu et al. (1995) revealed that flavonoid improved in barley and Kramer et al. (1991) also found increased content of polyamines in cucumber by UV-B radiation. Flavonols concentration also improved in Norway spruce (Picea abies) on UV-B exposure (Fischbach et al., 1999). Along similar lines, the increased production of the important anticancerous phenolic compounds, that is, vinblastine and vincristine, due to UV-B exposure in Catharanthus roseus has been reported by Bernard et al. (2009). Shiozaki et al. (1999) also revealed that flavonoids in the roots of pea plants was enhanced on UV (300 400 nm) exposure. Flavonols production was stimulated by UV-B in silver birch and grape leaves (Tegelberg et al., 2004). Moreover, photosynthetic pigments, condensed tannins were accumulated under six different daily doses of UV radiation (UV-A and UV-B), whereas its precursor, (1)-catechin, significantly decreased (Lavola et al., 2003). In a UV-tolerant rice cultivar, C-glycosylflavone contents increasingly appeared but were not found in a susceptible cultivar when exposed to different UV-B light levels (Markham et al., 1998). Furthermore, in several plant species, enhanced flavonoid levels have been measured at higher altitudes (Bachereau et al., 1998; Zidorn et al., 2005; Rieger et al., 2008; Spitaler et al.,
2008; Murai et al., 2009). It has been proven in several plant species that the expression of CHS is transcriptionally activated by UV light, which is the first enzyme in the flavonoid biosynthesis pathway (Koes et al., 1989; Schulze-Lefert et al., 1989).
9.4.2 Plant Phenolics and Their Role in Heavy Metal Stress Heavy metal toxicity is one of the important abiotic stresses that alter physiological and metabolic processes, thus leading to harmful effects in plants (Villiers et al., 2011). It has been reported that certain flavonoids exhibit the ability to provide heavy metal stress protection by transition metals chelation (e.g., Fe, Cu, Ni, Zn), which generates hydroxyl radical via Fenton’s reaction (Mira et al., 2002;Williams et al., 2004). Kidd et al. (2001) revealed that the chelation of these metals in the soil may be an effective form of defense against the effects of high metals concentration toxicity. Michalak (2006) observed that the biosynthesis of phenolic compounds that are precursors of lignin intensifies under stress conditions, for example, in plants subjected to heavy metal stress. Research on corn plants (Zea mays L.) confirmed this further when grown on soil contaminated with aluminum ions and root exudates were found with high levels of catechin and quercetin. Winkel-Shirley (2001) reported that flavonoids are involved in plants’ defense, growing in soils that are rich in toxic metals such as aluminum. The production of betalains in Beta vulgaris is stimulated by Cu21 (Trejo-Tapia et al., 2001). The hairy roots were exposed to metal ions to improve betalaines production (Thimmaraju and Ravishankar, 2004). Red cabbage seedlings accumulated phenolic compounds, total antioxidant capacity, and increased PAL activity when treated with copper (Posmyk et al., 2009). Accumulation of betacyanins in callus cultures of Amaranthus caudatus is stimulated by Cu21 (Obrenovic, 1990). Flavonoids accumulation was also observed in cell cultures of Ginkgo biloba treated with CuSO4 as compared with untreated cells (Kim et al., 1999). Similarly, association between concentration of CuSO4 and flavonoid level in cell cultures of Digitalis lanata was reported (Bota and Deliu, 2011). Nickel stress leads to significant decrease in anthocyanin levels as observed by Hawrylak et al. (2007). Michalak (2006) observed that plants with high content of tannins, such as tea, are able to tolerate high concentrations of manganese in a soil, as they are protected by the direct chelation of these ions. Lavid et al. (2001) reported the heavy metal ions binding with polyphenols in Nympheae where heavy metals (Hg, Pb, Cr) were chelating by the polyphenols rich methanol extract.
PLANT SIGNALING MOLECULES
9.4 PHENOLICS AND ABIOTIC STRESS TOLERANCE
9.4.3 Plant Phenolics and Their Role in Drought Stress Drought is the major abiotic stress that affects plant growth and development and causes losses in agricultural production. As has been reported by several studies, phenolics content increased in plants under water scarcity. Flavonoid accumulation is important to improve drought tolerance in wild-type and Arabidopsis thaliana mutants revealed by transcriptomic and metabolomic approaches (Nakabayashi et al., 2014). Ballizany et al. (2012) revealed that the quercetin (a flavonol) contents enhanced significantly in white clover under drought conditions, which was higher in the more drought-resistant genotypes. Kirakosyan et al. (2003) reported that under drought conditions, flavonols have been increased in other species also, such as Crataegus laevigata and Crataegus monogyna. Similarly, in Cistus clusii plants upon controlled drought treatments, and in plants collected from the field in summer, characterized by high temperatures and prolonged lack of rain in the Mediterranean climate, an increase in flavanol levels has been reported (Hernandez et al., 2004). Akula and Ravishankar (2011) reported that the defense mechanism against drought stress is triggered by bioactivity of leaf phenolic molecules. Phenolic acids and flavonoids as antioxidant accumulation and sunshields are involved in plants’ response to drought stress (Nichols et al., 2015). Larson (1988) also reported the increased level of flavonoids and phenolic acids in willow leaves under drought conditions causes oxidative stress. In droughtresistant tomato cultivars kaempferol and quercetin (flavonoids) were enhanced while reduced in drought sensitive cultivars reported by Sa´nchez-Rodrı´guez et al. (2011). In red-hulled and black-hulled rice the radical-scavenging ability depended on the concentrations of proanthocyanidins and anthocyanins, respectively (Oki et al., 2002). Flavonoids and phenolic acids were synthesized in a large amount in wheat leaves and cell-damaging oxidants also generated under drought stress (Ma et al., 2014). Chalker-Scott (1999) reported that plant tissues containing anthocyanins are usually rather resistant to drought. For example, a purple cultivar of chili resists water stress better than a green cultivar revealed by Bahler et al. (1991). In Chenopodium quinoa saponins content decreased from 0.46% to 0.38% dry weight (dw) in plants growing under low water deficit and in high water deficit conditions, respectively (Soliz-Guerrero et al., 2002). Phenolic compounds concentration was 10% improved in Hypericum brasiliense grown under drought stress as compared with control plants (De Abreu and Mazzafera, 2005). Similarly, phenolic compound were also increased in pea plants (Pisum sativum) when
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grown under drought conditions (Nogue’s et al., 1998). In both leaves and flowers of Tridax procumbens significant increases of total phenolic content were observed under drought stress (Gnanasekaran and Kalavathy, 2017). Antioxidant capacity of phenolic acids was reflected by change in their contents during the process of finger millet malting (Subba Rao and Muralikrishna, 2002). Nichols et al. (2015) reported that the high levels of flavonols, quercetin, and kaempferol contents were related with improved stress tolerance capacity of white clover under drought conditions.
9.4.4 Plant Phenolics and Their Role in Cold Stress It has been observed that nonfreezing low temperatures enhance phenolic metabolism in plants (Akula and Ravishankar, 2011). Phenolic metabolism is stimulated at a critical low temperature, which is the threshold temperature at which chilling injury is also induced (Janska et al., 2010). This low temperature results in cold-induced stimulation of the PAL activity (EC 4.3.1.5) as well as other enzymes necessary for phenolic biosynthesis, leading to increased phenolic production and modified plant development either independently or by interaction with known plant growth promoters, especially ethylene (Lattanzio et al., 1994, 2001). Cold stress increases phenolic production into the cell wall either as suberin or lignin (Griffith and Yaish, 2004). Lignification and suberin deposition increase resistance to cold stress. These cell wall thickenings protect the plant from freezing stress. An increase in cell wall thickening could reduce cell collapse during freezing-induced dehydration and mechanical stress, thus providing freezing resistance of the plant (Chalker-Scott and Fuchigami, 1989). Apple trees are found to be associated with high levels of chlorogenic acid as an adaptive measure to cold climate (Perez-Ilzarbe et al., 1997). Christie et al. (1994) reported the anthocyanins accumulation during cold stress and Pedranzani et al. (2003) reported that cold and water stresses initiated changes in endogenous jasmonates in Pinus.
9.4.5 Plant Phenolics and Their Role in Nutrient Stress Plant growth depends on the supply of recycled nutrients. External nutrient supply and nutrient mineralization by soil microorganisms contribute the nutrient requirements. The factors regulating nutrient cycle include climate, substrate (litter) quality, and decomposer organisms. Polyphenols influence the supply
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and flow of inorganic and organic soil nutrients available for plants and/or microbes. Phenolic compounds find their way to the soil as leachates from the aboveas well as below-ground parts of plants and/or within above and belowground plant litter (Ha¨ttenschwiler and Vitousek, 2000). Polyphenols affect the composition and activity of decomposers thus influencing the rates of decomposition and nutrient cycling (Lattanzio et al., 2006). Phenolic compounds show a sensitive response to nutrient deficiency, thus providing a method for diagnosing nutrient disorders prior to the appearance of visible symptoms. Deficiencies of N, P, K, and S usually result in increased concentrations of phenolic compounds, and abundant N generally inhibits phenolic accumulation (Gershenzon, 1913; McClue, 1977). Visual symptoms of N or P deficiency are red or purple tints of the leaves due to accumulation of anthocyanins (Hewitt, 1963). Nutrient stress increased threefold anthocyanidins level and doubled quercetin-3-Oglucoside in tomato (Bongue-Bartelsman Phillips, 1995). Osmotic stress by sucrose and other agents regulate anthocyanin production in Vitis vinifera cultures (Tuteja and Mahajan, 2007).
9.5 CONCLUSION AND FUTURE PROSPECTS Plant phenolics are the most common and widespread secondary metabolites, comprising a large reservoir of natural chemical diversity with a huge range of compounds and enzymes and a wide spectrum of mechanisms of gene regulation, and transport of metabolites and enzymes. Plants accumulate phenolic compounds in their tissues as an adaptive response to adverse environmental stresses including wounding, pathogen attack, mineral deficiencies, and temperature stress. Polyphenols modify the developmental status of the plant independently or by interacting with plant growth promoters like ethylene. Furthermore, these compounds, the precursors for lignin and suberin, are polymerized into the cell wall. These cell wall thickenings protect the plant from freezing stress. An increase in cell wall thickening could reduce cell collapse during freezing-induced dehydration and mechanical stress, thus providing freezing resistance of the plant (Chalker-Scott and Fuchigami, 1989). Polyphenols influence the supply and flow of inorganic and organic soil nutrients available for plants and/or microbes. They also show a sensitive response to nutrient deficiency, thus providing a method for diagnosing nutrient disorders prior to the appearance of visible symptoms.
Despite a handful of studies on biosynthesis of phenolic compounds and their accumulation as an adaptive response against abiotic stresses, studies on the proper mechanism of their accumulation and their interactions with other cell metabolites are desperately needed to develop a complete understanding of their increased expression and imparting tolerance under such circumstances.
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Wu, S., Chappell, J., 2008. Metabolic engineering of natural products in plants; tools of the trade and challenges for the future. Curr. Opin. Biotechnol. 19, 145 152. Yamasaki, H., Heshiki, R., Ikehara, N., 1995. Leaf-goldening induced by high light in Ficus microcarpa L. f., a tropical fig. J. Plant Res. 108, 171 180. Yamasaki, H., Takahashi, S., Heshiki, R., 1999. The tropical fig Ficus microcarpa L. f. cv. Golden Leaves lacks heat-stable dehydroascorbate reductase activity. Plant Cell Physiol. Zhu, J.K., 2016. Abiotic stress signalling and responses in plants. Cell 167 (2), 313 324. Zidorn, C., Schubert, B., Stuppner, H., 2005. Altitudinal differences in the contents of phenolics in flowering heads of three members of the tribe Lactuceae (Asteraceae) occurring as introduced species in New Zealand. Biochem. Syst. Ecol. 33, 855 872.
Further Reading Alscher, R.G., Donahue, H.L., Cramer, C.L., 1997. Reactive oxygen species and antioxidants: relationships in green cells. Physiol. Plant 100, 224 233. Blumthaler, M., Ambach, M., Ellinger, R., 1997. Increase in solar UV radiation with altitude. J. Photochem. Photobiol. B 39, 130 134. Draper, J., 1997. Salicylate, superoxide synthesis and cell suicide in plant defence. Trends Plant Sci. 2, 162 165. Lattanzio, V., Linsalata, V., Palmieri, S., Van Sumere, C.F., 1989. The beneficial effect of citric and ascorbic acid on the phenolic browning reaction in stored artichoke (Cynara scolymus L.) heads. Food Chem. 33, 93 106.
PLANT SIGNALING MOLECULES