Next Article in Journal
Manure Acidification and Air Cleaners for Ammonia Abatement: A Holistic Assessment of the Costs and Effects on Terrestrial, Freshwater and Marine Ecosystems
Next Article in Special Issue
Use of Multivariate Analysis in Screening for Drought Tolerance in Ornamental Asteraceae Species
Previous Article in Journal
Tara (Caesalpinia spinosa) in Natural and Agroforestry Systems under an Altitudinal Gradient in the Peruvian Andes: Responses to Soil and Climate Variation
Previous Article in Special Issue
Genome-Wide Identification, Structural Characterization, and Gene Expression Analysis of BES1 Transcription Factor Family in Tartary Buckwheat (Fagopyrum tataricum)
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Agronomy
Volume 13
Issue 2
10.3390/agronomy13020280
agronomy-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Interactions and Regulatory Functions of Phenolics in Soil-Plant-Climate Nexus

by
Deblina Misra
1,2,
Writuparna Dutta
1,
Gaurav Jha
3,4,* and
Puja Ray
1
1
Multitrophic Interactions and Biocontrol Research Laboratory, Department of Life Sciences, Presidency University, 86/1 College Street, Kolkata 700073, India
2
Department of Biology, New Mexico State University, Las Cruces, NM 88003, USA
3
Department of Agronomy, Kansas State University, Manhattan, KS 66506, USA
4
Department of Agricultural and Technology Education, Montana State University, Bozeman, MT 59715, USA
*
Author to whom correspondence should be addressed.
Agronomy 2023, 13(2), 280; https://doi.org/10.3390/agronomy13020280
Submission received: 1 November 2022 / Revised: 8 January 2023 / Accepted: 9 January 2023 / Published: 17 January 2023
(This article belongs to the Collection Abiotic Stress Tolerance in Plants: Towards a Sustainable Agriculture)
Browse Figures
Versions Notes

Abstract

:
Phenols are major compounds produced by plant species as a peripheral stimulus or as a regulatory defense mechanism under different environmental biotic stresses. These secondary metabolites are generated from shikimic and acetic acid metabolic pathways. The aromatic benzene ring compound plays an important role in plant development, especially in the defense forefront. They provide structural integrity and support to the plants. Phenolic phytoalexins released by pathogen/arthropod-attacked or wounded plants nullify or repel organisms for the advantage of the host. The allelopathic potential of phenolic compounds is observed in both natural and managed ecosystems. The global impacts of climatic variabilities such as drought, increased carbon dioxide, or greenhouse gas emissions alter the quantitative response of plant phenols. This review primarily discusses the different aspects of phenolic interactions concerning health, antioxidant properties, and insect-plant interaction as a nexus of soil and plant relations in response to variable climatic conditions.

1. Introduction

Primary plant metabolites, such as carbohydrates, amino and organic acids, and enzymes, exhibit essential physiological pathways such as glycolysis, the Krebs cycle, and the Calvin cycle that are important for plant growth, reproduction, and metabolism [1]. Metabolic pathways are enzyme-mediated chemical reactions and metabolites are organic compounds synthesized by the host [2]. In contrast, secondary metabolites such as phenols, alkaloids, flavonoids, and terpenoids play a significant role in stress and the defense mechanism of the plant [3] and are not directly associated with plant growth. They are responsible for attracting pollinators and seed dispersion [4,5] and are distributed within the taxonomic groups in the plant kingdom. The functions of secondary metabolites are particular to the plant species in which they occur [6]. The primary metabolites contribute to the production of secondary metabolites biosynthetically. Their deficiency does not cause dreadful effects on the plants [7]. The secondary metabolite content in plants is far less than the primary metabolites. Most of the facts, questioned by the shared efforts of photochemistry and plant physio-biology, depicted that secondary metabolite is a way out through which the plants respond to peripheral stimulus [8,9]. Bioactive compounds collected in plant tissues through biochemistry mechanisms are encrypted by other mechanisms of regulation. So, it is assumed that each plant species has progressed up to a remarkable set of machinery for the biosynthetic regulation of secondary metabolites, from previous generations, which effectively articulated these strategies [10]. Secondary metabolites provide (i) defense against other bacteria, fungi, amoebae, plants, insects, and large animals; (ii) metal transporting agents; (iii) agents of the relationship between microorganisms and plants, nematodes, insects, and higher animals; (iv) sexual hormones; and (v) differentiation effectors. Although antibiotics are not compulsory for sporulation, some secondary metabolites (including antibiotics) stimulate spore formation and inhibit or stimulate germination.
According to the British Nutrition Foundation, secondary metabolites are broadly divided into phenols, terpenoids, alkaloids, and sulphur-containing compounds [11]. Phenol and polyphenolic compounds are characterized by phenolic ring structure that includes flavonoids, lignans, and phenolic acids. Huge numbers of plant secondary metabolites validate the quest for bioactive and defensive compounds, which are elicitors and phytoalexins. One of the important compounds in the research area is known as capsidiol, present in tobacco leaves from Vitis vinifera, which is a terpenic ancestoral, aristolochene. It is seen in Nicotiana tabacum, among the diverse isoforms of terpene synthase, that the prenyl phosphate units are cyclized to form the aristolochene carbon form [12]. This bicyclic unit of alkene is designed as the most central biosynthetic step in the biogenesis of capsidiol. In this biosynthetic pathway, the terpene synthase transcripts level specifically is influenced by Manduca sexta infestation of shoots in Nicotiana attenuate leaves [13]. In this review, we discuss plant phenolics and their importance in soil-plant relations under global climatic variabilities. The manuscripts describe the need to integrate plant phenolics in agroecological systems, the biosynthetic pathways in plant systems, antioxidant properties, allelopathic interactions and their role in plant systems including the regulatory and inhibitory actions in the rhizosphere. We have also presented the agro-industrial integration of phenolic compounds and finally the impact of climate variabilities on the physiological and chemical fate of phenolics in plants.

2. Bio-Synthesis of Phenolic Compounds in Plant System

In response to several potential enemies in the vicinity, plants often produce secondary metabolites as their second line of defense, apart from the cuticle or/and the periderm, which acts as a physical barrier. Secondary metabolites produced by plants are usually phenolic in nature [14]. The two major metabolic pathways involved in synthesizing phenols in plants are the shikimate pathway and the malonate acetate pathway [15]. The seven enzymatic steps in the shikimate pathway (Figure 1) are the primary source of producing phenolic compounds, related to glycolysis (phenylalanine and tyrosine as end products; tryptophan as intermediate) in plants [16]. The important amino acids are produced in the plastid, clearly indicating the absence of such pathways in animal cells. Some of the steps of the pathway are also performed in the cytosol, where intermediate proteins and enzymes are also found. Apart from phenolic compounds, indole-3-acetic acid (IAA), tetrahydrofolate (vitamin B9), salicylic acid, some plant pigments, and quinones are also producing indole-3-acetic acid (IAA), tetrahydrofolate (vitamin B9), salicylic acid, and some plant pigments, and quinones other than the phenolic compounds are important components for transducing energy which is essential for electron transport chains in plant organs such as thylakoids and mitochondria [14,17]
The malonate acetate pathway is a comparatively less impactful biosynthesis pathway [18]. Phenylalanine ammonia-lyase (PAL) from the shikimic acid pathway catalyzes the production of phenolic compounds. Phenylalanine ammonia-lyase is a vital gateway enzyme in the secondary metabolic pathway, chief to the synthesis of phenolic compounds. It initiates the formation of cinnamic acid (CIN) from phenylalanine (Phe), important in regulating the formation of many phenolic acids [19]. The cell walls contain phenolic acid due to biotic stress, which increases the phenylpropanoid pathway where cinnamic acid and benzoic acid synthesis [20]. The PAL activity is hindered by 2-aminoindan-2-phosphonic acid (AIP) and is reported to have stronger inhibition capability in comparison to 2-aminooxyacetate (AOA) and 2 aminooxy-3-phenylpropanoic acid [21]. Due to the inhibitory effect of PAL by the enzyme AIP, there resulted in an accumulation of phenolic compounds in lettuce which limited browning in cut lettuce [22]. Another study reported a decrease in phenol accumulation in response to the inhibitory effect of PAL by AIP treatment [23]. The PAL also plays important role in producing phenol and flavonoids in response to biotic stresses in the fruiting bodies of the crops [24].

3. Antioxidant Properties of Phenols

Reactive oxygen species (ROS) are important signaling molecules and free radicals that respond to cell signaling in plants due to stress [25]. The most popular ROS are superoxide radical, hydrogen peroxide and hydroxyl radical originating from electron transfers to dioxygen [26]. Reactive oxygen species (ROS) increases due to an imbalance in cellular homeostasis to maintain balance [27]. Reactive oxygen species (ROS) and reactive nitrogen species (RNS) are produced continuously by normal cellular environmental factors and are extremely responsive to the oxidized molecule. This mode of action in the mitochondrial respiratory chain and inflammation might lead to damage to other biotic molecules, such as proteins and DNA [28,29,30]. To avoid this damage, plants develop enzymatic and non-enzymatic defense mechanisms in which antioxidant metabolites (and enzymes) neutralize ROS [31]. A variety of responses were drawn, where some authors found a correlation between the polyphenol content and the antioxidant activity, while others found no such relationship [32]. The author [33] mentioned a parallel increase between phenol content and antioxidant activity during the germination of Pangium edule Reinw, whereas [34] an increase in the antioxidant activity of lupin seed (Lupinus albus ssp. Graecus), was observed and phenolic compounds, peptides/amino acids, and phospholipids are responsible for this increased production [34]
There is an ambiguity in the correlation between the polyphenol content and the antioxidant activity [26]. In response to plant stress, flavonoid and phenylpropanoid compounds, present mostly in plant cell vacuoles and apoplast (exterior to plasma cell and within cell wall), detoxify hydrogen peroxide by donating electrons to guaiacol peroxidases and forming their respective phenoxyl radicals [35]. Dimers or trimers of flavonoids are produced due to oxidization (reaction I below) in H2O2-peroxidase (enzyme) system (Figure 2).
I
2FlavOH + H2O2 → 2FlavO·+ 2H2O
In this reversible cycle (reaction II below), the phenoxyl radicals (i.e., FlavO·) are converted to their phyto phenols (i.e., flavonols–FlavOH) in enzymatic presence of ascorbate (asc), delimiting the degradation of products [36] while in absence of (asc) polymerization products are produced irreversibly.
II
2FlavO + (asc) → 2FlavOH + 2MDA (monodehydroascorbate radical)
Monodehydroascorbate radical is transported to the cytoplasm and is reduced there by (Gsh)-dependent glutathione reductase (DHAR) to (asc) and dehydroascorbic acid (DHA) [37]
III
MDA + MDA → (asc) + DHA
Ascorbate regeneration by cytosolic DHA reductase (cDHAR) and Gsh-DHAR when coupled the flavonoids peroxidase system act as stress protectants by scavenging hydrogen peroxide, similar to ascorbate.
IV
Summary of the three steps of reaction: H2O2 + (asc) → 2H2O + DHA
Though phenols show antioxidant properties, the prolonged presence of phenoxyl radicals can be responsible for cell mortality [38]. Antagonistically, reports have shown that extracts from berries have shown the presence of anthocyanins, quercetin, esters of coumaric acid, etc. with anticancer efficacy against different human cell lines [39]. Inhibition in tumor growth due to the polyphenol content from tea extracts has been noteworthy while working with rat cell lines, holding epigallocatechin gallate and theaflavin as the responsible polyphenols [40,41]. Inhibition of tumours is brought about by apoptosis or cell cycle arrest. The cells usually then undergo DNA fragmentation or chromatin condensation. Polyphenols such as flavonoids such as quercetin, rutin, and apigenin, phenolics acids such as gallic acid, tannic acid, caffeic acid, as well as delphinidin, resveratrol, and curcumin have shown oxidative DNA strand breakage, bringing about apoptosis and with anti-cancer drug developing properties [39,42].

4. Role of Phenol and Phenolic Compounds in Plant Systems

Secondary metabolites secreted from plants are of great importance in defense growth, and development. They are associated with various processes together with rhizogenesis [43,44], resistance to biotic and abiotic stress, and redox reactions in soils [45]. Also, they are related to flowering pigments and act as constitutive guards against intruders. They play an important role as allelopathic compounds and signal molecules. These compounds have an important role as natural animal toxicants [46] and function as pesticides [47,48]. They are also useful constituents of the rhizosphere. For weed control, the compounds are recognized as allelochemicals and in animals as phytoestrogens [49]. Effective allelochemicals can be present as volatile terpenoids, contaminated water-soluble hydroquinone, hydroxycinnamates, and 5-hydroxynapthoquinone. Several simple and complex phenolic compounds accumulated in plant tissues act as phytoalexins, phytoanticipins, and nematicides against many pathogens and insects [50]. Phenolic compounds have been used to serve as a valuable alternative to the chemical control of pathogens in crops.
When infection is caused by micro symbionts such as rhizobium as well as pathogen attack, then the herbivory phenols are synthesized and released [51]. These metabolites intra- and extra-cellular to plant tissues are known to function as phytoalexins, phytoanticipins, and node gene inducers. Many studies showed that phenolic metabolites are toxic to plants and a level determined in a higher range affects soils [52,53,54,55]. Phenolic acid concentrations in soil can range from 2.1% to 4.4% for monocot roots and from 0.1% to 0.6% for dicot roots [56]. The phenolics might have a beneficial or negative impact on the availability of plant mineral elements in the rhizosphere. Through rainfall leachate of phenolic as chromogenic acid or through a variety of other methods that alter phenolic synthesis, green leaves and decomposing plant litter can regulate the rhizosphere and dynamics [56]. The development of protein complexes delays the decomposition and mineralization of organic matter, increases microbial activity when utilized as a carbon source, results in immobilization, and directly inhibits nitrification [57,58,59,60,61]. The effects of soil-borne diseases in modern agricultural systems may help varied defense mechanisms used by rhizosphere-dwelling plants. The effects of soil-borne diseases in modern agricultural systems may help varied defense mechanisms used by rhizosphere-dwelling plants. The production, release, and addition of numerous phenolic chemicals serve as the plant’s defense mechanism against diseases, nematodes, and phytophagous insects [62,63]. The alfalfa root releases isoflavonoid 2-(35-dihydroxyphenyl)-5, 6-dihydroxybenzofuran which acts as a phytoalexin to defend against root infections such as Fusarium oxysporum f. sp. Phaseoli [64]. When released into the soil through seeds, roots, or residue decomposition, these chemicals play a significant role in defense and protection against soil-borne diseases and root-feeding insects [18,65]. Due to the ecological potential of these macromolecules from symbiotic legumes in the rhizosphere as a sustainable method of lowering soil-borne diseases in the ecosystems, they have attracted more scientific interest [66].

5. Regulatory and Inhibitory Interactions of Phenolic Compounds in the Rhizospheric Soil Matrix

Phenolic compounds enter the soil systems as exudates from roots or as leachates or particulate matter from plants [67,68]. The release of phenolic compounds from decomposing leaf litter and roots on upper soil layers of the horizon is mediated by soil microbes. Phenolic compounds in soils exist in three forms—free or dissolved, absorbed or reversibly bound by clay minerals or chelated complexes with metals and proteins, and polymerized [67]. In soil formation and pedogenesis, phenolics and other organic molecules from the root and seed exudates, leaf leachates, and decaying plant residues play a key role. The degradation of phenols and their reactivity depends on the chemical structure and forms of phenol [69,70]. Many phenolics such as phenolic acids and tannins are water-soluble. These forms remain in solution between soil particles leading to reversible sorption through hydrophobic, hydrogen, and ionic interactions. These microbial condensation and polymerization reactions of phenolic compounds with amino acids and proteins in the soil matrix release soil organic acids of higher molecular weights such as fulvic acids, humic acids, and humin [60,71,72]. This process of humification alters the physicochemical processes in soils based on alterations in soil health and qualitative characteristics. The resulting humic substances are generated by polymeric combinations of phenolic compounds and soil organic matter [67]. The recalcitrant structure of phenols makes them resistant to natural biodegradation and decomposition. However, the phenolic compounds are highly soluble in water up to 10g L−1 [73]. These properties possess serious risks of environmental pollution [74,75,76].
The phenolic compounds are also known for inhibiting the oxidation of ammonia by nitrifying microorganisms during nitrification [77,78,79]. Contrastingly, low contents of phenolic acids in rhizospheric soils have indicated increased nitrogen (N) mineralization rates, and enhancement in ammonium content, resulting in increased conservation of soil N [80]. Contrastingly, phenolic compounds can enhance the mobility of soil phosphorus (P) depending on soil properties such as pH and organic chelates. The addition of phenolic compounds decreases the pH of saturation paste extract of calcareous and aluminum-dominated soils [81]. Phenols synergized with organic acids (chelates before biodegradation) alter the stable and sparingly soluble forms of soil phosphorus (P) to easily dissolvable forms [81]. The abundance of phenols can absorb large quantities of heavy metals such as cadmium in soils [82].
These abundances can lead to ecological consequences in the growth and development of plants, mainly impacting the germination stage. In woodland or forestry, regenerative practices and reforestation problems are attributed to the phenolic compounds polymerized with high organic matter and deposited in the soils. These depositions can be due to former tree species [81]. The phenolic compounds also impact other physiological responses during plant growth such as cellular expansion, membrane permeability, nutrient mobility, soil-plant relations for respiration, and water uptake [83].

6. Phenolic Compounds in Plant-Pathogen Interaction

Plant phenols constitute one of the common and important groups of defensive secondary metabolites compounds, that play a vital role against herbivores, including insects [71,84,85]. Insect attacks or defense mechanisms alter and elevate the qualitative and quantitative measures and elevation in activities of the oxidative enzyme [84]. For example, lignin is a phenolic heteropolymer and plays a significant role in plant defense against insects and pathogens [86] by physically blocking or increasing the leaf toughness, diminishing the nutritional content of the leaf, and restricting the entry of pathogens and feeding behaviour of herbivores (Figure 3) [87]. Lignin synthesis is induced by herbivore or pathogen attack and the rapid deposition reduces further growth of the pathogen or herbivore productivity. Some genes involved in lignin expression, such as (CAD/CAD-like genes) at times, are noted to increase in amount when studied on plants infected with pests and pathogens [86]. Due to the phenolic oxidation catalyzed by polyphenol oxidase (PPO) and peroxidase (POD), there is a potential defense mechanism in plants. To leaf proteins, the quinones are formed due to the oxidation of phenols binding covalently, and also hinder protein digestion in herbivores [88]. Also, quinones show direct toxicity to insects [88,89]. The nutritional value of plant proteins for insects is reduced due to the alkylation of amino acids, which in turn adversely affects insect growth and development [88]. Other than the mentioned roles there is evidence showing the role of phenols in the cyclic reduction in ROS such as superoxide anion and hydroxyl radicals, H2O2, and singlet oxygen, which activate a cascade of reactions leading to the activation of defensive enzymes [8]. Operophtera brumata (L.) in Salix leaves, the simple phenolics (salicylates) act as an antifeedant, and there is an adverse correlation between the salicylate levels and the larval growth; still, salicylic acid (SA) is much more important as phytohormone than as deterrent [90].
Some phenolic compounds are soluble in organic solvents, whereas some are soluble in water, such as carboxylic acid and glycosides [91]. Phenolics also play important by attracting pollinators and fruit dispersers, absorbing harmful ultraviolet radiation as a mechanical support in the plant, and limiting the growth of nearby competing plants [92]. There are a wide number of examples of phenolics used in defense against insect herbivores. Wheat cultivars which contain phenolic compounds are much less attractive to Rhopalosiphum padi (Cereal aphid) [93]. Catechol-based phenolics present in the leaves of Fragaria (strawberry) provide resistance to Tetranychus urticae (two-spotted spider mite) [94]. It is noticed that the cotton phenolic pigment gossypol has repellent effects against abundant insects and is lethal to Heliothis virescens (tobacco bollworm), Heliothis zea (bollworm), and quite a few other insects [95].

7. Allelopathic Interactions

Allelochemicals mostly spread via the roots and soil of plants many biotic and abiotic factors contribute to the allelopathic interactions among organisms. Phosphorus, nitrogen content, water stress, temperature, and microbes and their metabolites play a role of high significance [96,97]. Soil fatigue is a phenomenon in agriculture where the accumulation of fungi secreting mycotoxins in the soil hinders the productivity of plants [98]. Such toxins have an upper hand in the soil-microbes-plant interaction and have survived or endured in the community interaction with a myriad of biological effects [99]. These mycotoxins vary in their potential impact on plants and/or animals, belonging to various groups of cyclic terpenoids, polyketides, and cyclic polypeptides [100]. Polyketides include many potent mycotoxins with not only zootoxic but also phytotoxic properties: alternariol from Alternaria spp., aflatoxin from Aspergillus spp., fumigatin and zearalenone from Fusarium spp., trichodermin from Trichoderma spp., patulin, citrinin, rubratoxin from Penicillium spp. [98]. Microorganisms in interaction with plant and soil secrete a large number of allelochemicals (lytic enzymes such as glucanases, chitinases, etc.) and influence and causes several plant diseases. β-1,3-glucanase among many other cell wall degrading enzymes (CWDEs), destroys the cell walls causing the root rot Pythium aphanidermatum and the fusarial rot Fusarium oxysporum [99,101].
Among various metabolic compounds secreted by plants in response to interaction, phenols play a major role and constitute a major group of plant allelochemicals in the ecosystem (Figure 4) [102]. Phenolic allelochemicals play a role in root elongation, observed in Lactuca sativa L. [103] by cell division, and interfering with the development of the plant [104] growth of wheat (Triticum aestivum var. PBW) has been significantly reduced when their seeds were soaked in root leachates or root and leaf extract of various weeds such as Parthenium hysterophorus, Asphodelus tenuifolius, and Pluchea lanceolata, revealing a high phenolic content [105].
The phenolic allelochemicals based on their structure can be broadly divided into the following categories [107] (Table 1).

8. Phenolic Compounds from Agro-Industrial Byproducts

From agricultural and industrial residues, the abundance of phenolic compounds and their extraction and antioxidant activity has been widely researched [110]. Several agricultural byproducts have been identified which contain phenolic compounds with antioxidant activity such as rice hulls, [111] buckwheat hulls, [112] and almond hulls [113]. The total cinnamic acid content of the hulls of Swedish oats (Avena sativa L.) [114] was found higher than that of the groats (23.6 compared to 3.6 mg kg−1 dry matter) [115]. Another source of phenolic antioxidants is pistachio hulls, which may contain up to 34 mg tannic acid equivalents phenolics/g dry weight [115].
Citrus industry byproducts, if utilized, could be key sources of phenolic compounds, as the peels in particular have been found to contain advanced amounts of total phenolics in comparison to the edible portions [116]. Phenolic compounds, various phenolic acids, and flavonoids are present in tomato waste [117]. There are reports that dry onion skin waste is one of the agro-industrial wastes which is high in flavonoids and phenolic acids and has a role in antioxidant activity [118]. Similarly, potato, which is one of the most widely used vegetables around the world, has been reported to have peel waste that has glycoalkaloids [119].
Another important source of phenolic compounds is the byproducts of the olive industry, with much attention focused on olive mill wastes. In the olive fruits, the phenolic compounds are distributed into the olive oil or may be present in the aqueous phase wastewater or the solid phase pomace, with nearly 1–2% partitioning into the former [120]. Therefore, a major potential source of phenolics, particularly in consideration that annual production exceeds 7 million tons, is the olive mill wastes [121]. The phenolic content of the olive mill wastewater (OMWW) is reported to vary between 1.0% and 1.8% depending on varietal factors and processing effects. Hydroxytyrosol, tyrosol, oleuropein, and a variety of hydroxycinnamic acids are major components of OMWW [122]. Olive leaves are another byproduct of the olive industry and can be also referred to as a source of phenolics, though to a lesser extent [123] there are some reports where it is mentioned that wines made from blueberries have higher total phenolic content (600–1860 mg Gallic acid equivalents L−1) than white wines (191–306 mg Gallic acid equivalents L−1) [124]. Collectively, the information provided gives an outline idea about phenols and phenolic compounds related to agro-waste and its impact.

9. Phenol as Contaminants

Phenols are organic contaminants present and regarded as one of the most toxic pollutants in wastewater; they are harmful to organisms at low concentrations and many of them have been classified as hazardous pollutants with direct harmful effects on human health at low concentrations [125,126]. Oil refineries and the petrochemical industry, tanneries, olive mills, cork-producing industry, and pulp and paper mills, contribute to the use and disinfectants of the pesticide [127,128,129,130]. Phenols are extensively distributed as environmental pollutants. From many industrial processes, including synthetic rubber, plastics, paper, oil refineries, petrochemical, ceramic, steel, conversion processes, and phenolic resin industries, the concentration of phenolic compounds varies widely. Natural forest fires are also a source of phenol contamination [131]. Phenol’s presence in water and wastewater could be toxic to plants if this water is reused for irrigation, while it may also be toxic for bacteria as well [126,132]. There is a serious discharge problem due to their poor biodegradability, high toxicity, and ecological aspects when wastewater containing phenolic compounds is discharged [133]. Industrial use is gradually avoided due to the high toxicity of phenols; they are subjected to specific regulations by substituting them with harmless compounds [134]. A crucial step is taken by the Environmental Protection Agency (EPA) which calls for lowering the phenol content in the wastewater to less than 1mg L−1 [134]. Wastewaters containing phenols and other toxic compounds need careful treatment before discharge into the receiving bodies of water. Additionally, biological treatment, activated carbon adsorption, solvent extraction, chemical oxidation, and electrochemical methods are the most widely used methods for removing phenol and phenolic compounds from wastewater [135,136,137].

10. Response of Phenolics to Climate Change

Plant growth and physiological functions are globally impacted by climate change. Elevated levels of CO2, temperature together with phytopathogenic infection or arthropod herbivory significantly modify plant biochemistry and likewise their defense responses. By the year 2100, the global mean surface temperature is predicted to increase by at least 1.5 degrees Celsius compared to that in 1850–1900 [138]. Plant phenolics play an important role in plant protection against abiotic stressors due to climatic variabilities such as drought, salinity, and ultraviolet (UV) radiations [139,140]. These stressors increase the expression of phenolic compounds and impact decomposition and nutrient cycling [140,141]. Plants originating from a cold climate, higher altitude, or semi-arid environment have been reported to have the highest phenolic compound contents in their organs [142]. The strong oxidant property of phenolic compounds protects the cellular structure by increasing ROS production and avoiding cell damage [143,144]. Increased production of polyphenols by many plant species is indicative of protection against oxidative damage by drought [145]. Depending on the plant genotype and water deficit conditions, phenolic compounds such as tannins and flavonoids are synthesized to protect the cell membrane and photosynthesis mechanism, protein denaturation, and plant growth inhibition [146,147]. The study by Varela and colleagues measured polyphenols in shrublands and detected variability in concentrations of phenolic compounds among different species of Patagonian shrublands [145]. In Larrea divaricata production of phenolic compound, synthesis increased during the season of greatest drought, while Larrea chilense has lower production of phenolic compounds without variation between seasons. Similarly, another group of scientists experimented on five different genotypes of peanuts to study the impact of drought on phenolic compounds where drought significantly increased the phenolic content in leaves and stems at midseason [148].
Globally, climatic variabilities particularly increased temperature, are strongly correlated to increased carbon dioxide in the atmosphere [149]. In plant systems, increased temperature and elevated carbon dioxide levels increase phenolic compounds in foliar tissues and decrease concentrations in woody parts of the plants. Drought and UV radiations influence the accumulation of phenolic compounds in some cultivars of Solanaceous and leafy vegetables [150,151,152]. Salt stress in soils is also a major environmental stressor due to climate change. The salinity stress can significantly reduce the photosynthetic electron chain reaction and can promote ROS leading to oxidative stress in plants [153]. The phenolic compounds such as flavonoids and pro-anthocyanidins play an important role by acting as free radical scavengers [154]. The flavonoid accumulation induced by UV-B radiations protects the cellular system by potentially acting as a ROS scavenger [143,154,155].
Climate plays a key role in the biochemical contents of fruits and plants, leading to variation in the phenolic content of the same species of different regions [156]. Besides the climate impacts on the plant, the field performance of any microbial herbicide in terms of virulence and host range depends on several biological traits of the organisms and their environmental conditions, which directly and indirectly can leave ecological and economic consequences on the mutually interacting species [157].

11. Conclusions

Secondary metabolites such as phenols and polyphenolic compounds are regulatory and have inhibitory effects on plants in response to abiotic stresses or external stimuli. It generates defense mechanisms against harmful microbiota, chelating transport agents, sexual hormones, and differentiation effectors. These compounds provide significant benefits for human health and therefore the manuscript provides a forum to understand the nexus benefits of plant phenols as an integrative balance of soil, rhizosphere, plant, and climate change. The redoximorphic features of phenolic hormones concerning plant hormones (such as resveratrol (which improves impaired glucose) and streptozotocin (beneficial impacts on β-cells)) play a vital role in chronic metabolic disorders in humans. Therefore, understanding the biosynthetic pathway and the mechanism of phenolic compounds in agroecological systems is important for further research and development in this area.
The two major biosynthetic pathways—shikimic acid and malonic acetate pathways—are primary sources of producing phenolic compounds, followed by the glycolytic pathway and cinnamic acid which are the intermediate product. The polyphenolic compounds enhance vegetable products’ nutritional and functional values and further evolve into strong complexation with digestive enzymes when consumed. The presence in plants makes phenolic compounds as precursors during the decomposition of soil organic matter specifically for humic acid in soils.
This leads to the synergistic impact of these secondary metabolites as functions of pedogenetic processes in soil. The defense mechanism against feeding herbivores and allelopathic interaction is majorly in response to the release of phenolic compounds. Phenolic compounds are impacted by variable climate and inductive or natural stresses such as drought and salinity. These stresses impact the physicochemical mechanisms of phenols, primarily increasing the reactive oxygen species. Therefore, the beneficial impacts of phenolic compounds as integrative balance in soil and plant systems, presented in this study concerning global climatic changes, aim to advance further research of these compounds under external environmental stimuli or abiotic stresses.

Author Contributions

Conceptualization, D.M., W.D. and G.J.; writing—original draft, D.M., W.D. and G.J.; writing—reviewing and editing, D.M., W.D., G.J. and P.R.; visualization, W.D.; funding acquisition, G.J.; supervision, P.R.; project administration, D.M., W.D. and G.J. All authors have read and agreed to the published version of the manuscript.

Funding

The APC was supported by the College of Agriculture, Montana State University, Bozeman, MT (USA).

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Choudhary, S.; Singh Tanwer, B.; Vijayvergia, R.; Singh, T. Preliminary phytochemical screening and primary metabolites of Melothria maderaspatana (Linn.) Cong. Int. J. Biol. Pharm. Res. 2013, 4, 168–171. [Google Scholar]
  2. Wolfe, N.L.; Hoehamer, C.F.; Mccutcheon, S.C.; Schnoor, J.L. Enzymes Used by Plants and Microorganisms to Detoxify Organic Compounds. In A Wiley-Interscience Series of Texts and Monographs; McCutcheon, S.C., Schnoor, J.L., Eds.; John Wiley & Sons, Inc.: Hoboken, NJ, USA, 2004; pp. 159–187. [Google Scholar] [CrossRef]
  3. Nicholson, R.L.; Hammerschmidt, R. Phenolic Compounds and their Role in Disease Resistance. Annu. Rev. Phytopathol. 2003, 369–389. [Google Scholar] [CrossRef]
  4. Crozier, A.; Clifford, M.; Ashihara, H. Plant Secondary Metabolites: Occurrence, Structure and Role in The Human Diet. Q. Rev. Biol. 2014, 82, 151. [Google Scholar] [CrossRef]
  5. Seigler, D.S. Plant Secondary Metabolism; Springer: New York, NY, USA, 1998. [Google Scholar] [CrossRef]
  6. Hounsome, N.; Hounsome, B.; Tomos, D.; Edwards-Jones, G. Plant Metabolites and Nutritional Quality of Vegetables. J. Food. Sci. 2008, 73, R48–R65. [Google Scholar] [CrossRef]
  7. Irchhaiya, R.; Kumar, A.; Yadav, A.; Gupta, N.; Kumar, S.; Gupta, N.; Kumar, S.; Yadav, V.; Prakash, A.; Gurjar, H. Metabolites In Plants and Its Classification. World. J. Pharm. Pharm. Sci. 2015, 4, 287–305. [Google Scholar]
  8. Maffei, M.E.; Mithöfer, A.; Boland, W. Before Gene Expression: Early Events in Plant–Insect Interaction. Trends. Plant. Sci 2007, 12, 310–316. [Google Scholar] [CrossRef]
  9. Rasmann, S.; Turlings, T.C.J.; Rasmann, S.; Turlings, T.C.J. First Insights into Specificity of Belowground Tritrophic Interactions. Oikos 2008, 117, 362–369. [Google Scholar] [CrossRef] [Green Version]
  10. Shitan, N. Secondary Metabolites in Plants: Transport and Self-Tolerance Mechanisms. Biosci. Biotechnol. Biochem. 2016, 80, 1283–1293. [Google Scholar] [CrossRef] [Green Version]
  11. Goldberg, G.; British Nutrition Foundation. Plants: Diet and Health: The Report of a British Nutrition Foundation Task Force; Cambridge University Press: Cambridge, UK, 2003; p. 347. [Google Scholar]
  12. Maldonado-Bonilla, L.D.; Betancourt-Jiménez, M.; Lozoya-Gloria, E. Local and Systemic Gene Expression of Sesquiterpene Phytoalexin Biosynthetic Enzymes in Plant Leaves. Eur. J. Plant. Pathol. 2008, 121, 439–449. [Google Scholar] [CrossRef]
  13. Bohlmann, J.; Stauber, E.J.; Krock, B.; Oldham, N.J.; Gershenzon, J.; Baldwin, I.T. Gene Expression of 5-Epi-Aristolochene Synthase and Formation of Capsidiol in Roots of Nicotiana attenuata and N. sylvestris. Phytochemistry 2002, 60, 109–116. [Google Scholar] [CrossRef]
  14. Marchiosi, R.; dos Santos, W.D.; Constantin, R.P.; de Lima, R.B.; Soares, A.R.; Finger-Teixeira, A.; Mota, T.R.; de Oliveira, D.M.; Foletto-Felipe, M.d.P.; Abrahão, J.; et al. Biosynthesis and Metabolic Actions of Simple Phenolic Acids in Plants. Phytochem. Rev. 2020, 19, 865–906. [Google Scholar] [CrossRef]
  15. Hättenschwiler, S.; Vitousek, P.M. The Role of Polyphenols in Terrestrial Ecosystem Nutrient Cycling. Trends. Ecol. Evol. 2000, 15, 238–242. [Google Scholar] [CrossRef] [PubMed]
  16. Herrmann, K.M. The Shikimate Pathway: Early Steps in the Biosynthesis of Aromatic Compounds. Plant. Cell 1995, 7, 907. [Google Scholar] [CrossRef] [PubMed]
  17. Maeda, H.; Dudareva, N. The Shikimate Pathway and Aromatic Amino Acid Biosynthesis in Plants. Annu. Rev. Plant. Biol. 2012, 63, 73–105. [Google Scholar] [CrossRef]
  18. Mandal, S.M.; Chakraborty, D.; Dey, S. Phenolic Acids Act as Signaling Molecules in Plant-Microbe Symbioses. Plant. Signal. Behav. 2010, 5, 359–368. [Google Scholar] [CrossRef] [Green Version]
  19. Koukol, J.; Conn, E.E. The Metabolism of Aromatic Compounds in Higher Plants: IV. Purification and Properties of the Phenylalanine Deaminase of Hordeum vulgare. J. Biol. Chem. 1961, 236, 2692–2698. [Google Scholar] [CrossRef]
  20. de Oliveira, D.M.; Finger-Teixeira, A.; Rodrigues Mota, T.; Salvador, V.H.; Moreira-Vilar, F.C.; Correa Molinari, H.B.; Craig Mitchell, R.A.; Marchiosi, R.; Ferrarese-Filho, O.; Dantas dos Santos, W. Ferulic Acid: A Key Component in Grass Lignocellulose Recalcitrance to Hydrolysis. Plant. Biotechnol. J. 2015, 13, 1224–1232. [Google Scholar] [CrossRef]
  21. Appert, C.; Zoń, J.; Amrhein, N. Kinetic Analysis of the Inhibition of Phenylalanine Ammonia-Lyase by 2-Aminoindan-2-Phosphonic Acid and other Phenylalanine Analogues. Phytochemistry 2003, 62, 415–422. [Google Scholar] [CrossRef]
  22. Hisaminato, H.; Murata, M.; Homma, S. Relationship between the Enzymatic Browning and Phenylalanine Ammonia-Lyase Activity of Cut Lettuce, and the Prevention of Browning by Inhibitors of Polyphenol Biosynthesis. Biosci. Biotechnol. Biochem. 2001, 65, 1016–1021. [Google Scholar] [CrossRef] [Green Version]
  23. Keski-Saari, S. Phenolic Compounds in Birch Seedlings during Early Ontogeny: Regulation of Biosynthesis and Accumulation in Response to Nutrient Availability and UV-B Radiation. Ph.D. Thesis, University of Joensuu, Joensuu, Finland, 2005. [Google Scholar]
  24. Ghasemzadeh, A.; Ghasemzadeh, N. Flavonoids and Phenolic Acids: Role and Biochemical Activity in Plants and Human. J. Med. Plant. Res. 2011, 5, 6697–6703. [Google Scholar] [CrossRef]
  25. Sies, H.; Jones, D.P. Reactive Oxygen Species (ROS) as Pleiotropic Physiological Signalling Agents. Nat. Rev. Mol. Cell. Biol. 2020, 21, 363–383. [Google Scholar] [CrossRef] [PubMed]
  26. Michalak, A. Phenolic Compounds and Their Antioxidant Activity in Plants Growing under Heavy Metal Stress. Pol. J. Environ. Stud. 2006, 15, 523–530. [Google Scholar]
  27. Sharma, P.; Jha, A.B.; Dubey, R.S.; Pessarakli, M. Reactive Oxygen Species, Oxidative Damage, and Antioxidative Defense Mechanism in Plants under Stressful Conditions. J. Bot. 2012, 2012, 217037. [Google Scholar] [CrossRef] [Green Version]
  28. Lea, A.J.; Tung, J.; Zhou, X. A Flexible, Efficient Binomial Mixed Model for Identifying Differential DNA Methylation in Bisulfite Sequencing Data. PLoS Genet 2015, 11, e1005650. [Google Scholar] [CrossRef] [Green Version]
  29. Urso, M.L.; Clarkson, P.M. Oxidative Stress, Exercise, and Antioxidant Supplementation. Toxicology 2003, 189, 41–54. [Google Scholar] [CrossRef]
  30. Halliwell, B. Effect of Diet on Cancer Development: Is Oxidative DNA Damage a Biomarker? Free. Radic. Biol. Med. 2002, 32, 968–974. [Google Scholar] [CrossRef]
  31. Shin, S.Y.; Kim, I.S.; Kim, Y.S.; Lee, H.; Yoon, H.S. Ectopic Expression of Brassica rapa L. MDHAR Increased Tolerance to Freezing Stress by Enhancing Antioxidant Systems of Host Plants. S. Afr. J. Bot. 2013, 88, 388–400. [Google Scholar] [CrossRef] [Green Version]
  32. Lafka, T.I.; Sinanoglou, V.; Lazos, E.S. On the Extraction and Antioxidant Activity of Phenolic Compounds from Winery Wastes. Food. Chem. 2007, 104, 1206–1214. [Google Scholar] [CrossRef]
  33. Andarwulan, N.; Fardiaz, D.; Wattimena, G.A.; Shetty, K. Antioxidant Activity Associated with Lipid and Phenolic Mobilization during Seed Germination of Pangium edule Reinw. J. Agric. Food. Chem. 1999, 47, 3158–3163. [Google Scholar] [CrossRef]
  34. Tsaliki, E.; Lagouri, V.; Doxastakis, G. Evaluation of the Antioxidant Activity of Lupin Seed Flour and Derivatives (Lupinus. albus ssp. graecus). Food. Chem. 1999, 65, 71–75. [Google Scholar] [CrossRef]
  35. Takahama, U.; Oniki, T. Flavonoids and Some Other Phenolics as Substrates of Peroxidase: Physiological Significance of the Redox Reactions. J. Plant. Res. 2000, 113, 301–309. [Google Scholar] [CrossRef]
  36. Yamasaki, H.; Sakihama, Y.; Ikehara, N. Flavonoid-Peroxidase Reaction as a Detoxification Mechanism of Plant Cells against H2O2. Plant. Physiol. 1997, 115, 1405–1412. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  37. Takahama, U.; Oniki, T. A Peroxidase/Phenolics/Ascorbate System can Scavenge Hydrogen Peroxide in Plant Cells. Physiol. Plant 1997, 101, 845–852. [Google Scholar] [CrossRef]
  38. Sakihama, Y.; Cohen, M.F.; Grace, S.C.; Yamasaki, H. Plant Phenolic Antioxidant and Prooxidant Activities: Phenolics-Induced Oxidative Damage Mediated by Metals in Plants. Toxicology 2002, 177, 67–80. [Google Scholar] [CrossRef] [PubMed]
  39. Dai, J.; Mumper, R.J. Plant Phenolics: Extraction, Analysis and their Antioxidant and Anticancer Properties. Molecules 2010, 15, 7313–7352. [Google Scholar] [CrossRef] [PubMed]
  40. Inhibition of Lung Carcinogenesis by Black Tea in Fischer Rats Treated with a Tobacco-Specific Carcinogen: Caffeine as an Important Constituent1|Cancer Research|American Association for Cancer Research. Available online: https://aacrjournals.org/cancerres/article/58/18/4096/504549/Inhibition-of-Lung-Carcinogenesis-by-Black-Tea-in (accessed on 31 October 2022).
  41. Effects of Tea, Decaffeinated Tea, and Caffeine on UVB Light-Induced Complete Carcinogenesis in SKH-1 Mice: Demonstration of Caffeine as a Biologically Important Constitutent of Tea1|Cancer Research|American Association for Cancer Research. Available online: https://aacrjournals.org/cancerres/article/57/13/2623/503367/Effects-of-Tea-Decaffeinated-Tea-and-Caffeine-on (accessed on 31 October 2022).
  42. Eghbaliferiz, S.; Iranshahi, M. Prooxidant Activity of Polyphenols, Flavonoids, Anthocyanins and Carotenoids: Updated Review of Mechanisms and Catalyzing Metals. Phytother. Res. 2016, 30, 1379–1391. [Google Scholar] [CrossRef]
  43. Curir, P.; VanSumere, C.F.; Termini, A.; Barthe, P.; Marchesini, A.; Dolci, M. Flavonoid Accumulation Is Correlated with Adventitious Roots Formation in Eucalyptus gunnii Hook Micropropagated through Axillary Bud Stimulation. Plant. Physiol. 1990, 92, 1148–1153. [Google Scholar] [CrossRef] [Green Version]
  44. Kevers, C.; Coumans, M.; Coumans-Gillès, M.-F.; Caspar, T. Physiological and Biochemical Events Leading to Vitrification of Plants Cultured in vitro. Physiol. Plant 1984, 61, 69–74. [Google Scholar] [CrossRef]
  45. Talaat, I.M.; Khattab, H.I.; Ahmed, A.M. Changes in Growth, Hormones Levels and Essential Oil Content of Ammi. visnaga L. Plants Treated with Some Bioregulators. Saudi. J. Biol. Sci. 2014, 21, 355–365. [Google Scholar] [CrossRef] [Green Version]
  46. Takahama, U. Oxidation of Vacuolar and Apoplastic Phenolic Substrates by Peroxidase: Physiological Significance of the Oxidation Reactions. Phytochem. Rev. 2004, 3, 207–219. [Google Scholar] [CrossRef]
  47. Rice, E.L. Allelopathy—An Overview. In Chemically Mediated Interactions between Plants and Other Organismss; Springer: Boston, MA, USA, 1985; pp. 81–105. [Google Scholar] [CrossRef]
  48. Vidhyasekaran, P. Physiology of Disease Resistance in Plants; CRC Press, Inc.: Boca Raton, FL, USA, 1988; Volume 2. [Google Scholar]
  49. Waterman, P.G.; Mole, S. Extrinsic Factors Influencing Production of Secondary Metabolites in Plants. In Insect-Plant Interactions; CRC Press: Boca Raton, FL, USA, 2019; pp. 107–134. [Google Scholar] [CrossRef]
  50. Akhtar, M.; Malik, A. Roles of Organic Soil Amendments and Soil Organisms in the Biological Control of Plant-Parasitic Nematodes: A Review. Bioresour. Technol. 2000, 74, 35–47. [Google Scholar] [CrossRef]
  51. Lawson, C.G.R.; Rolfe, B.G.; Djordjevic, M.A. Rhizobium Inoculation Induces Condition-Dependent Changes in the Flavonoid Composition of Root Exudates from Trifolium subterraneum. Funct. Plant. Biol. 1996, 23, 93–101. [Google Scholar] [CrossRef]
  52. Patrick, Z.A.; Patrick, A.Z. Phytotoxic Substances Associated with the Decomposition in Soil of Plant Residues. Soils 1971, 111, 13–18. [Google Scholar] [CrossRef]
  53. Lodhi, M.A.K. Soil-Plant Phytotoxicity and its Possible Significance in Patterning of Herbaceous Vegetation in a Bottomland Forest. Am. J. Bot. 1975, 62, 618–622. [Google Scholar] [CrossRef]
  54. Chou, C.H.; Lin, H.J. Autointoxication Mechanism of Oryza sativa I. Phytotoxic Effects of Decomposing Rice Residues in Soil. J. Chem. Ecol. 1976, 2, 353–367. [Google Scholar] [CrossRef]
  55. Elliott, L.F.; Cheng, H.H. Assessment of Allelopathy among Microbes and Plants; American Chemical Society: Washington, DC, USA, 1987; pp. 504–515. [Google Scholar] [CrossRef]
  56. Makoi, J.H.J.R.; Ndakidemi, P.A. Biological, Ecological and Agronomic Significance of Plant Phenolic Compounds in Rhizosphere of the Symbiotic Legumes. Afr. J. Biotechnol. 2010, 6, 1358–1368. [Google Scholar] [CrossRef]
  57. Fog, K. The Effect of Added Nitrogen on the Rate of Decomposition of Organic Matter. Biol. Rev. 1988, 63, 433–462. [Google Scholar] [CrossRef]
  58. Castells, E. Indirect Effects of Phenolics on Plant Performance by Altering Nitrogen Cycling: Another Mechanism of Plant-Plant Negative Interactions. In Allelopathy in Sustainable Agriculture and Forestry; Springer: New York, NY, USA, 2008; pp. 137–156. [Google Scholar] [CrossRef]
  59. Phoenix, A Model of The Dynamics of Carbon and Nitrogen in Grassland Soils on JSTOR. Available online: https://www.jstor.org/stable/45128653#metadata_info_tab_contents (accessed on 25 December 2022).
  60. Kuiters, A.T. Role of Phenolic Substances from Decomposing Forest Litter in Plant-Soil Interactions. Acta. Bot. Neerl. 1990, 39, 329–348. [Google Scholar] [CrossRef]
  61. Das, N.; Chandran, P. Microbial Degradation of Petroleum Hydrocarbon Contaminants: An Overview. Biotechnol. Res. Int. 2011, 2011, 941810. [Google Scholar] [CrossRef] [Green Version]
  62. Bennett, R.N.; Wallsgrove, R.M. Secondary Metabolites in Plant Defence Mechanisms. New. Phytol. 1994, 127, 617–633. [Google Scholar] [CrossRef]
  63. The Chemical Defenses of Plants to Pathogens and Herbivores on JSTOR. Available online: https://www.jstor.org/stable/2096863#metadata_info_tab_contents (accessed on 25 December 2022).
  64. Yoneyama, K.; Natsume, M. Allelochemicals for Plant–Plant and Plant–Microbe Interactions. Compr. Nat. Prod. II. Chem. Biol. 2010, 4, 539–561. [Google Scholar] [CrossRef]
  65. Dakora, F.D. Defining New Roles for Plant and Rhizobial Molecules in Sole and Mixed Plant Cultures Involving Symbiotic Legumes. New. Phytol. 2003, 158, 39–49. [Google Scholar] [CrossRef]
  66. Singh, R.K.; Kumar, D.P.; Singh, P.; Solanki, M.K.; Srivastava, S.; Kashyap, P.L.; Kumar, S.; Srivastava, A.K.; Singhal, P.K.; Arora, D.K. Multifarious Plant Growth Promoting Characteristics of Chickpea Rhizosphere Associated Bacilli Help to Suppress Soil-Borne Pathogens. Plant. Growth. Regul. 2014, 73, 91–101. [Google Scholar] [CrossRef]
  67. Min, K.; Freeman, C.; Kang, H.; Choi, S.U. The Regulation by Phenolic Compounds of Soil Organic Matter Dynamics under a Changing Environment. Biomed. Res. Int. 2015, 2015. [Google Scholar] [CrossRef] [Green Version]
  68. Schmidt, M.A.; Halvorson, J.J.; Hagerman, A.E.; Gonzalez, J.M. Macronutrients and Metals Released from Soils by Solutions of Naturally Occurring Phenols. J. Plant. Nutr. Soil. Sci. 2017, 180, 544–553. [Google Scholar] [CrossRef]
  69. Grilli, E.; di Resta, E.; Scognamiglio, M.; Pacifico, S.; Fiorentino, A.; Nogueira, T.A.R.; Vigliotti, R.C.; Ganga, A. Soil Phenolic Compound Variability in Two Mediterranean Olive Groves. Plant. Soil. Environ. 2020, 66, 207–215. [Google Scholar] [CrossRef]
  70. Schmidt, M.W.I.; Torn, M.S.; Abiven, S.; Dittmar, T.; Guggenberger, G.; Janssens, I.A.; Kleber, M.; Kögel-Knabner, I.; Lehmann, J.; Manning, D.A.C.; et al. Persistence of Soil Organic Matter as an Ecosystem Property. Nature 2011, 478, 49–56. [Google Scholar] [CrossRef]
  71. Rani, P.U.; Jyothsna, Y. Biochemical and Enzymatic Changes in Rice Plants as a Mechanism of Defense. Acta. Physiol. Plant 2010, 32, 695–701. [Google Scholar] [CrossRef]
  72. Suflita, J.M.; Bollag, J.-M. Polymerization of Phenolic Compounds by a Soil-Enzyme Complex. Soil. Sci. Soc. Am. J. 1981, 45, 297–302. [Google Scholar] [CrossRef]
  73. Bajaj, M.; Gallert, C.; Winter, J. Phenol Degradation Kinetics of an Aerobic Mixed Culture. Biochem. Eng. J. 2009, 46, 205–209. [Google Scholar] [CrossRef]
  74. Biodegradation Kinetics of Benzene, Toluene, and Phenol as Single and Mixed Substrates for Pseudomonas putida F1.|Semantic Scholar. Available online: https://www.semanticscholar.org/paper/Biodegradation-kinetics-of-benzene%2C-toluene%2C-and-as-Reardon-Mosteller/d1f912457207a500e71c334fd48b07ea2f126a6c (accessed on 24 October 2022).
  75. Ma, F.; Shi, S.N.; Sun, T.H.; Li, A.; Zhou, J.T.; Qu, Y.Y. Biotransformation of Benzene and Toluene to Catechols by Phenol Hydroxylase from Arthrobacter sp. W1. Appl. Microbiol. Biotechnol. 2013, 97, 5097–5103. [Google Scholar] [CrossRef] [PubMed]
  76. Chen, J.; Zhang, L.; Jin, Q.; Su, C.; Zhao, L.; Liu, X.; Kou, S.; Wang, Y.; Xiao, M. Bioremediation of Phenol in Soil through Using a Mobile Plant-Endophyte System. Chemosphere 2017, 182, 194–202. [Google Scholar] [CrossRef] [PubMed]
  77. Wang, J.; Zhang, Y.; Yan, N.; Chen, J.; Rittmann, B.E. Enhanced Phenol Bioavailability by Means of Photocatalysis. Biodegradation 2013, 24, 597–602. [Google Scholar] [CrossRef] [PubMed]
  78. Grunditz, C.; Dalhammar, G. Development of Nitrification Inhibition Assays Using Pure Cultures of Nitrosomonas and Nitrobacter. Water. Res. 2001, 35, 433–440. [Google Scholar] [CrossRef]
  79. McCarty, G.W.; Bremner, J.M.; Schmidt, E.L. Effects of Phenolic Acids on Ammonia Oxidation by Terrestrial Autotrophic Nitrifying Microorganisms. FEMS Microbiol. Lett. 1991, 85, 345–349. [Google Scholar] [CrossRef]
  80. Chen, L.C.; Guan, X.; Wang, Q.K.; Yang, Q.P.; Zhang, W.D.; Wang, S.L. Effects of Phenolic Acids on Soil Nitrogen Mineralization over Successive Rotations in Chinese Fir Plantations. J. For. Res. (Harbin.) 2020, 31, 303–311. [Google Scholar] [CrossRef]
  81. Hu, H.; Tang, C.; Rengel, Z. Influence of Phenolic Acids on Phosphorus Mobilisation in Acidic and Calcareous Soils. Plant. Soil. 2005, 268, 173–180. [Google Scholar] [CrossRef]
  82. Li, J.; Liu, J.; Lu, H.; Jia, H.; Yu, J.; Hong, H.; Yan, C. Influence of the Phenols on the Biogeochemical Behavior of Cadmium in the Mangrove Sediment. Chemosphere 2016, 144, 2206–2213. [Google Scholar] [CrossRef]
  83. Adeboye, P.T.; Bettiga, M.; Olsson, L. The Chemical Nature of Phenolic Compounds Determines Their Toxicity and Induces Distinct Physiological Responses in Saccharomyces cerevisiae in Lignocellulose Hydrolysates. AMB Express 2014, 4, 46. [Google Scholar] [CrossRef] [Green Version]
  84. War, A.R.; Paulraj, M.G.; War, M.Y.; Ignacimuthu, S. Jasmonic Acid-Mediated-Induced Resistance in Groundnut (Arachis Hypogaea L.) Against Helicoverpa armigera (Hubner) (Lepidoptera: Noctuidae). J. Plant. Growth. Regul. 2011, 30, 512–523. [Google Scholar] [CrossRef]
  85. Sharma, H.C.; Sujana, G.; Manohar Rao, D. Morphological and Chemical Components of Resistance to Pod Borer, Helicoverpa. armigera in Wild Relatives of Pigeon pea. Arthropod. Plant. Interact 2009, 3, 151–161. [Google Scholar] [CrossRef] [Green Version]
  86. Barakat, A.; Bagniewska-Zadworna, A.; Frost, C.J.; Carlson, J.E. Phylogeny and Expression Profiling of CAD and CAD-like Genes in Hybrid Populus (P. deltoides × P. nigra): Evidence from Herbivore Damage for Subfunctionalization and Functional Divergence. BMC Plant. Biol. 2010, 10, 1–11. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  87. Johnson, M.T.J.; Smith, S.D.; Rausher, M.D. Plant Sex and the Evolution of Plant Defenses against Herbivores. Proc. Natl. Acad. Sci. USA 2009, 106, 18079–18084. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  88. Bhonwong, A.; Stout, M.J.; Attajarusit, J.; Tantasawat, P. Defensive Role of Tomato Polyphenol Oxidases against Cotton Bollworm (Helicoverpa. armigera) and Beet Armyworm (Spodoptera exigua). J. Chem. Ecol. 2009, 35, 28–38. [Google Scholar] [CrossRef]
  89. Duffey, S.S.; Stout, M.J. Antinutritive and Toxic Components of Plant Defense Against Insects. Arch. Insect. Biochem. Physiol. 1996, 32, 3. [Google Scholar] [CrossRef]
  90. Simmonds, M.S.J. Flavonoid-Insect Interactions: Recent Advances in Our Knowledge. Phytochemistry 2003, 64, 21–30. [Google Scholar] [CrossRef]
  91. Abebe, W. Review on Plant Defense Mechanisms Against Insect Pests. Int. J. Nov. Res. Interdiscip. Stud. 2021, 8, 15–39. [Google Scholar]
  92. Cheeke, P.R. Toxicants of Plant Origin; CRC Press: Boca Raton, FL, USA, 1989; ISBN 9780849369933. [Google Scholar]
  93. Wójcicka, A. Introduction Cereal Phenolic Compounds as Biopesticides of Cereal Aphids. J. Environ. Stud. 2010, 19, 1337–1343. [Google Scholar]
  94. Luczynski, A.; Isman, M.B.; Raworth, D.A. Strawberry Foliar Phenolics and Their Relationship to Development of the Twospotted Spider Mite. J. Econ. Entomol. 1990, 83, 557–563. [Google Scholar] [CrossRef]
  95. Maxwell, F.G.; Lafever, H.N.; Jenkins, J.N. Blister Beetles on Glandless Cotton. J. Econ. Entomol. 1965, 58, 792–793. [Google Scholar] [CrossRef]
  96. Baldwin, I.T. Mechanism of Damage-Induced Alkaloid Production in Wild Tobacco. J. Chem. Ecol. 1989, 15, 1661–1680. [Google Scholar] [CrossRef] [PubMed]
  97. Sugiyama, A.; Yazaki, K. Root Exudates of Legume Plants and Their Involvement in Interactions with Soil Microbes; Springer: Berlin/Heidelberg, Germany, 2012; pp. 27–48. [Google Scholar] [CrossRef]
  98. Berestetskiy, A.O. A Review of Fungal Phytotoxins: From Basic Studies to Practical Use. Appl. Biochem. Microbiol. 2008, 44, 453–465. [Google Scholar] [CrossRef]
  99. Polyak, Y.M.; Sukcharevich, V.I. Allelopathic Interactions between Plants and Microorganisms in Soil Ecosystems. Biol. Bull. Rev. 2020, 9, 562–574. [Google Scholar] [CrossRef]
  100. Daguerre, Y.; Siegel, K.; Edel-Hermann, V.; Steinberg, C. Fungal Proteins and Genes Associated with Biocontrol Mechanisms of Soil-Borne Pathogens: A Review. Fungal. Biol. Rev. 2014, 28, 97–125. [Google Scholar] [CrossRef]
  101. Chatterton, S.; Punja, Z.K.; Chatterton, S. Chitinase and Beta-1,3-Glucanase Enzyme Production by the Mycoparasite Clonostachys. rosea f. catenulata against Fungal Plant Pathogens. Can. J. Microbiol. 2009, 55, 356–367. [Google Scholar] [CrossRef]
  102. Inderjit. Plant Phenolics in Allelopathy. Botanical. Rev. 1996, 62, 186–202. [Google Scholar] [CrossRef]
  103. Li, H.H.; 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]
  104. John, J.; Sarada, S. Role of Phenolics in Allelopathic Interactions “Statistical Models for Profit Maximization of Homesteads in Kerala” View Project Nutrient Budgeting, Bio-Resource Recycling, Microbial Dynamics and Disease Mapping in Integrated Farming Systems of Wayanad District View Project Role of Phenolics in Allelopathic Interactions. Allelopath. J. 2012, 29, 215–230. [Google Scholar]
  105. Rice, E.L. Some Roles of Allelopathic Compounds in Plant Communities. Biochem. Syst. Ecol 1977, 5, 201–206. [Google Scholar] [CrossRef]
  106. Bhatla, S.C.; Lal, M.A. Plant Physiology, Development and Metabolism; Springer: Berlin/Heidelberg, Germany, 2018; pp. 1–1237. [Google Scholar] [CrossRef]
  107. Hoang Anh, L.; van Quan, N.; Tuan Nghia, L.; Dang Xuan, T. Phenolic Allelochemicals: Achievements, Limitations, and Prospective Approaches in Weed Management. Weed. Biol. Manag. 2021, 21, 37–67. [Google Scholar] [CrossRef]
  108. Chai, T.T.; Ooh, K.F.; Ooi, P.W.; Chue, P.S.; Wong, F.C. Leucaena leucocephala Leachate Compromised Membrane Integrity, Respiration and Antioxidative Defence of Water Hyacinth Leaf Tissues. Bot. Stud. 2013, 54, 8. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  109. Yoshida, S.; Asami, T.; Kawano, T.; Yoneyama, K.; Crow, W.D.; Paton, D.M.; Takahashi, N. Photosynthetic Inhibitors in Eucalyptus grandis. Phytochemistry 1988, 27, 1943–1946. [Google Scholar] [CrossRef]
  110. Moure, A.; Cruz, J.M.; Franco, D.; Manuel Domínguez, J.; Sineiro, J.; Domínguez, H.; Núñez, M.J.; Carlos Parajó, J. Natural Antioxidants from Residual Sources. Food. Chem. 2001, 72, 145–171. [Google Scholar] [CrossRef]
  111. Ramarathnam, N.; Osawa, T.; Namiki, M.; Kawakishi, S. Chemical Studies on Novel Rice Hull Antioxidants. 2. Identification of Isovitexin, A C-Glycosyl Flavonoid. J. Agric. Food. Chem. 1989, 37, 316–319. [Google Scholar] [CrossRef]
  112. Watanabe, M.; Ohshita, Y.; Tsushida, T. Antioxidant Compounds from Buckwheat (Fagopyrum esculentum Möench) Hulls. J. Agric. Food. Chem. 1997, 45, 1039–1044. [Google Scholar] [CrossRef]
  113. Takeoka, G.R.; Dao, L.T. Antioxidant Constituents of Almond [Prunus dulcis (Mill.) D.A. Webb] Hulls. J. Agric. Food. Chem. 2003, 51, 496–501. [Google Scholar] [CrossRef]
  114. Bryngelsson, S.; Mannerstedt-Fogelfors, B.; Kamal-Eldin, A.; Andersson, R.; Dimberg, L.H. Lipids and Antioxidants in Groats and Hulls of Swedish Oats (Avena sativa L.). J. Sci. Food. Agric. 2002, 82, 606–614. [Google Scholar] [CrossRef]
  115. Balasundram, N.; Sundram, K.; Samman, S. Phenolic Compounds in Plants and Agri-Industrial by-Products: Antioxidant Activity, Occurrence, and Potential Uses. Food. Chem. 2006, 99, 191–203. [Google Scholar] [CrossRef]
  116. Gorinstein, S.; Martín-Belloso, O.; Park, Y.S.; Haruenkit, R.; Lojek, A.; Íž, M.; Caspi, A.; Libman, I.; Trakhtenberg, S. Comparison of Some Biochemical Characteristics of Different Citrus Fruits. Food. Chem. 2001, 74, 309–315. [Google Scholar] [CrossRef]
  117. Ćetković, G.; Savatović, S.; Čanadanović-Brunet, J.; Djilas, S.; Vulić, J.; Mandić, A.; Četojević-Simin, D. Valorisation of Phenolic Composition, Antioxidant and Cell Growth Activities of Tomato Waste. Food. Chem. 2012, 133, 938–945. [Google Scholar] [CrossRef]
  118. Volpi, C.; Bartolini, D.; Brighenti, V.; Galli, F.; Tiecco, M.; Pellati, F.; Clementi, C.; Sardella, R. Antioxidant Power on Dermal Cells by Textiles Dyed with an Onion (Allium cepa L.) Skin Extract. Antioxidants 2021, 10, 1655. [Google Scholar] [CrossRef] [PubMed]
  119. Wijngaard, H.H.; Ballay, M.; Brunton, N. The Optimisation of Extraction of Antioxidants from Potato Peel by Pressurised Liquids. Food. Chem. 2012, 133, 1123–1130. [Google Scholar] [CrossRef]
  120. Rodis, P.S.; Karathanos, V.T.; Mantzavinou, A. Partitioning of Olive Oil Antioxidants between Oil and Water Phases. J. Agric. Food. Chem. 2002, 50, 596–601. [Google Scholar] [CrossRef]
  121. Ranalli, A.; Lucera, L.; Contento, S. Antioxidizing Potency of Phenol Compounds in Olive Oil Mill Wastewater. J. Agric. Food. Chem. 2003, 51, 7636–7641. [Google Scholar] [CrossRef] [PubMed]
  122. Obied, H.K.; Allen, M.S.; Bedgood, D.R.; Prenzler, P.D.; Robards, K.; Stockmann, R. Bioactivity and Analysis of Biophenols Recovered from Olive Mill Waste. J. Agric. Food. Chem. 2005, 53, 823–837. [Google Scholar] [CrossRef] [PubMed]
  123. Benavente-García, O.; Castillo, J.; Lorente, J.; Ortuño, A.; del Rio, J.A. Antioxidant Activity of Phenolics Extracted from Olea. europaea L. Leaves. Food. Chem. 2000, 68, 457–462. [Google Scholar] [CrossRef]
  124. Sánchez-Moreno, C.; Larrauri, J.A.; Saura-Calixto, F. Free Radical Scavenging Capacity and Inhibition of Lipid Oxidation of Wines, Grape Juices and Related Polyphenolic Constituents. Food. Res. Int. 1999, 32, 407–412. [Google Scholar] [CrossRef]
  125. Tepe, O.; Dursun, A.Y. Combined Effects of External Mass Transfer and Biodegradation Rates on Removal of Phenol by Immobilized Ralstonia eutropha in a Packed Bed Reactor. J. Hazard. Mater 2008, 151, 9–16. [Google Scholar] [CrossRef]
  126. Stefanakis, A.; Akratos, C.S.; Tsihrintzis, V.A. Vertical Flow Constructed Wetlands: Eco-Engineering Systems for Wastewater and Sludge Treatment. In Vertical Flow Constructed Wetlands: Eco-engineering Systems for Wastewater and Sludge Treatment; Elsevier: Amsterdam, The Netherlands, 2014; pp. 1–378. [Google Scholar] [CrossRef]
  127. Abdelwahab, O.; Amin, N.K.; El-Ashtoukhy, E.S.Z. Electrochemical Removal of Phenol from Oil Refinery Wastewater. J. Hazard. Mater. 2009, 163, 711–716. [Google Scholar] [CrossRef]
  128. Costa, C.R.; Botta, C.M.R.; Espindola, E.L.G.; Olivi, P. Electrochemical Treatment of Tannery Wastewater Using DSA Electrodes. J. Hazard. Mater. 2008, 153, 616–627. [Google Scholar] [CrossRef]
  129. Herouvim, E.; Akratos, C.S.; Tekerlekopoulou, A.; Vayenas, D.v. Treatment of Olive Mill Wastewater in Pilot-Scale Vertical Flow Constructed Wetlands. Ecol. Eng. 2011, 37, 931–939. [Google Scholar] [CrossRef]
  130. Abira, M.A.; van Bruggen, J.J.A.; Denny, P. Potential of a Tropical Subsurface Constructed Wetland to Remove Phenol from Pre-Treated Pulp and Papermill Wastewater. Water. Sci. Technol. 2005, 51, 173–176. [Google Scholar] [CrossRef]
  131. Stottmeister, U.; Kuschk, P.; Wiessner, A. Full-Scale Bioremediation and Long-Term Monitoring of a Phenolic Wastewater Disposal Lake. Pure. Appl. Chem. 2010, 82, 161–173. [Google Scholar] [CrossRef] [Green Version]
  132. Nair, C.I.; Jayachandran, K.; Shashidhar, S. Biodegradation of Phenol. Afr. J. Biotechnol. 2010, 7, 4951–4958. [Google Scholar] [CrossRef]
  133. Kennedy, L.J.; Vijaya, J.J.; Kayalvizhi, K.; Sekaran, G. Adsorption of Phenol from Aqueous Solutions Using Mesoporous Carbon Prepared by Two-Stage Process. Chem. Eng. J. 2007, 132, 279–287. [Google Scholar] [CrossRef]
  134. Palma, M.S.A.; Paiva, J.L.; Zilli, M.; Converti, A. Batch Phenol Removal from Methyl Isobutyl Ketone by Liquid–Liquid Extraction with Chemical Reaction. Chem. Eng. Process. Process. Intensif. 2007, 46, 764–768. [Google Scholar] [CrossRef]
  135. Annadurai, G.; Juang, R.S.; Lee, D.J. Microbiological Degradation of Phenol Using Mixed Liquors of Pseudomonas putida and Activated Sludge. Waste. Manag. 2002, 22, 703–710. [Google Scholar] [CrossRef]
  136. Mohan, D.; Chander, S. Single Component and Multi-Component Adsorption of Metal Ions by Activated Carbons. Colloids. Surf. A Physicochem. Eng. Asp. 2001, 177, 183–196. [Google Scholar] [CrossRef]
  137. Dursun, G.; Çiçek, H.; Dursun, A.Y. Adsorption of Phenol from Aqueous Solution by Using Carbonised Beet Pulp. J. Hazard. Mater. 2005, 125, 175–182. [Google Scholar] [CrossRef]
  138. Sihi, D.; Dari, B.; Kuruvila, A.P.; Jha, G.; Basu, K. Explainable Machine Learning Approach Quantified the Long-Term (1981–2015) Impact of Climate and Soil Properties on Yields of Major Agricultural Crops Across CONUS. Front. Sustain. Food. Syst. 2022, 6, 1–17. [Google Scholar] [CrossRef]
  139. Hunter, M.D. The Phytochemical Landscape; Princeton University Press: Princeton, NJ, USA, 2016. [Google Scholar]
  140. Moreira, X.; Roberts, L.A.; Galvez, M.D.H.; González, C.V.; Ramos, I.M.P. Micro-Climatic Effects on Plant Phenolics at the Community Level in a Mediterranean Savanna. Sci. Rep. 2020, 10, 14757. [Google Scholar] [CrossRef] [PubMed]
  141. Han, C.; Li, J.; Jin, P.; Li, X.; Wang, L.; Zheng, Y. The Effect of Temperature on Phenolic Content in Wounded Carrots. Food. Chem. 2017, 215, 116–123. [Google Scholar] [CrossRef]
  142. Zargoosh, Z.; Ghavam, M.; Bacchetta, G.; Tavili, A. Effects of Ecological Factors on the Antioxidant Potential and Total Phenol Content of Scrophularia striata Boiss. Sci. Rep. 2019, 9, 16021. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  143. Agati, G.; Tattini, M. Multiple Functional Roles of Flavonoids in Photoprotection. New Phytol. 2010, 186, 786–793. [Google Scholar] [CrossRef] [PubMed]
  144. Hatier, J.H.B.; Gould, K.S. Foliar Anthocyanins as Modulators of Stress Signals. J. Theor. Biol. 2008, 253, 625–627. [Google Scholar] [CrossRef]
  145. Varela, M.C.; Arslan, I.; Reginato, M.A.; Cenzano, A.M.; Luna, M.V. Phenolic Compounds as Indicators of Drought Resistance in Shrubs from Patagonian Shrublands (Argentina). Plant. Physiol. Biochem. 2016, 104, 81–91. [Google Scholar] [CrossRef]
  146. Schmidt, D.D.; Voelckel, C.; Hartl, M.; Schmidt, S.; Baldwin, I.T. Specificity in Ecological Interactions. Attack from the Same Lepidopteran Herbivore Results in Species-Specific Transcriptional Responses in Two Solanaceous Host Plants. Plant. Physiol. 2005, 138, 1763–1773. [Google Scholar] [CrossRef]
  147. de Sousa Araújo, T.A.; de Almeida e Castro, V.T.N.; da Silva Solon, L.G.; da Silva, G.A.; das Graças Almeida, M.; da Costa, J.G.M.; de Amorim, E.L.C.; Albuquerque, U.P. Does Rainfall Affect the Antioxidant Capacity and Production of Phenolic Compounds of an Important Medicinal Species? Ind. Crops. Prod. 2015, 76, 550–556. [Google Scholar] [CrossRef]
  148. Aninbon, C.; Jogloy, S.; Vorasoot, N.; Patanothai, A.; Nuchadomrong, S.; Senawong, T. Effect of End of Season Water Deficit on Phenolic Compounds in Peanut Genotypes with Different Levels of Resistance to Drought. Food. Chem. 2016, 196, 123–129. [Google Scholar] [CrossRef]
  149. Goudriaan, J.; Unsworth, M.H. Implications of Increasing Carbon Dioxide and Climate Change for Agricultural Productivity and Water Resources. Impact. Carbon. Dioxide. Trace. Gases. Clim. Chang. Glob. Agric. 2016, 53, 111–130. [Google Scholar] [CrossRef] [Green Version]
  150. Klunklin, W.; Savage, G. Effect on Quality Characteristics of Tomatoes Grown under Well-Watered and Drought Stress Conditions. Foods 2017, 6, 56. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  151. Rajabbeigi, E.; Eichholz, I.; Beesk, N.; Ulrichs, C.; Kroh, L.W.; Rohn, S.; Huyskens-Keil, S. Interaction of Drought Stress and UV-B Radiation-Impact on Biomass Production and Flavonoid Metabolism in Lettuce (Lactuca sativa L.). J. Appl. Bot. Food. Qual. 2013, 86, 190–197. [Google Scholar] [CrossRef]
  152. Živanović, B.; Vidović, M.; Milić Komić, S.; Jovanović, L.; Kolarž, P.; Morina, F.; Veljović Jovanović, S. Contents of Phenolics and Carotenoids in Tomato Grown under Polytunnels with Different UV-Transmission Rates. Turk. J. Agric. For. 2017, 41, 113–120. [Google Scholar] [CrossRef]
  153. Waśkiewicz, A.; Muzolf-Panek, M.; Goliński, P. Phenolic Content Changes in Plants under Salt Stress; Springer: New York, NY, USA, 2013. [Google Scholar]
  154. Sztatelman, O.; Grzyb, J.; Gabryś, H.; Banaś, A.K. The Effect of UV-B on Arabidopsis Leaves Depends on Light Conditions after Treatment. BMC Plant. Biol. 2015, 15, 281. [Google Scholar] [CrossRef] [Green Version]
  155. Kusano, M.; Tohge, T.; Fukushima, A.; Kobayashi, M.; Hayashi, N.; Otsuki, H.; Kondou, Y.; Goto, H.; Kawashima, M.; Matsuda, F.; et al. Metabolomics Reveals Comprehensive Reprogramming Involving Two Independent Metabolic Responses of Arabidopsis to UV-B Light. Plant. J. 2011, 67, 354–369. [Google Scholar] [CrossRef]
  156. Eseberri, I.; Trepiana, J.; Léniz, A.; Gómez-García, I.; Carr-Ugarte, H.; González, M.; Portillo, M.P. Variability in the Beneficial Effects of Phenolic Compounds: A Review. Nutrients 2022, 14, 1925. [Google Scholar] [CrossRef]
  157. Classen, A.E.T.; Sundqvist, M.K.; Henning, J.A.; Newman, G.S.; Moore, J.A.M.; Cregger, M.A.; Moorhead, L.C.; Patterson, C.M.; Sundqvist, M.K.; Henning, J.A.; et al. Direct and Indirect Effects of Climate Change on Soil Microbial and Soil Microbial-Plant Interactions: What Lies Ahead? Ecosphere 2015, 6, 1–21. [Google Scholar] [CrossRef]
Agronomy 13 00280 g001 550
Figure 1. Biosynthesis of phenolic compounds in the plant cell [14,15,16,17,18,19,20,21,22,23,24].
Figure 1. Biosynthesis of phenolic compounds in the plant cell [14,15,16,17,18,19,20,21,22,23,24].
Agronomy 13 00280 g001
Agronomy 13 00280 g002 550
Figure 2. Schematic diagram of scavenging mechanism of flavonoids or polyphenols [26,35,36,37].
Figure 2. Schematic diagram of scavenging mechanism of flavonoids or polyphenols [26,35,36,37].
Agronomy 13 00280 g002
Agronomy 13 00280 g003 550
Figure 3. Changes in the biochemical composition of the plants (infected or attacked by arthropods or pathogens) attract or repel other agents to the affected host plant [86,87].
Figure 3. Changes in the biochemical composition of the plants (infected or attacked by arthropods or pathogens) attract or repel other agents to the affected host plant [86,87].
Agronomy 13 00280 g003
Agronomy 13 00280 g004 550
Figure 4. Plants use allelopathy by their roots to absorb more nutrients along with water from the soil and eventually hinder the growth of neighbouring plants. Pathogen or arthropod attacks also bring about biochemical changes in the host plant indirectly [102,103,104,105]. The cationic changes brought about by the release of allelochemicals in the soil redirect the change in the nutrient uptake of the effector plant [106].
Figure 4. Plants use allelopathy by their roots to absorb more nutrients along with water from the soil and eventually hinder the growth of neighbouring plants. Pathogen or arthropod attacks also bring about biochemical changes in the host plant indirectly [102,103,104,105]. The cationic changes brought about by the release of allelochemicals in the soil redirect the change in the nutrient uptake of the effector plant [106].
Agronomy 13 00280 g004
Table
Table 1. Phenolic allele-chemical compounds and their mode of action.
Table 1. Phenolic allele-chemical compounds and their mode of action.
Phenolic CompoundsSome Examples with Their StructureFunction or Mechanism of ActionReference
C6 compounds
Simple Phenols
  • Resorcinol
  • Phloroglucinol
  • Catechol
  • Hydroquinone
Agronomy 13 00280 i001Have various inhibitory effects against enzyme activities. Catechol acts as inhibitors of phosphorylase. The acylphloroglucinol structure might play a significant role in inhibiting plant transpiration.[107,108]
C6-Cn compounds
n = 1
  • Shikimic acid
  • Benzoic acid and derivatives
  • Phenolic aldehydes
  • Phenolic glycosides
n = 2
  • Phenylacetic acids
  • Acetophenones
  • Styrenes
  • Phenethylamines
n = 3
  • Cinnamic acid and derivatives
  • Phenolic glycosides
  • Phenolic propanoids
  • Coumarins
  • Furanocoumarins
  • Aromatic amino acids
n = 4
  • Naphthoquinone
  • Phenylbutyric acids
Agronomy 13 00280 i002Effect on membrane permeability hormonal activity, respiration, photosynthetic activity, synthesis of organic compounds and plant growth as a whole[108]
C6-Cn-C6 compounds n = 2
  • Anthraquinones
n = 3
  • Flavones
  • Flavanones
  • Flavonols
  • Catechins
  • Epicatechins
  • Flavan-3,4-diols
  • Pterocarpanes
  • Flavonoid glycosides
Agronomy 13 00280 i003Inhibit the germination of seeds and growth of plants. Release of flavonoid compounds into the rhizosphere plays an important role in the supply of phosphorus to plants.[97]
Phenolic dimers
(C6-C3)2 Compounds
  • Coumaric acids and derivatives
(C6-C3-C6)2 compounds
  • Biflavonoids and poly flavonoids
Phenolic hybrids(C6-C1)10 Compounds
  • Tannins
Agronomy 13 00280 i004Tannic acid is an inhibitor of peroxidase, catalase, and cellulase [97]
Others
  • Phenolic monoterpenes
  • Phenolic lipids
  • Phenolic sesquiterpenes
  • Dibenzofurans
  • Quinolines
  • Benzoxazinones
Agronomy 13 00280 i005Effect on all mitosis stages, respiration, and membrane permeability[108,109]
C6 compounds—Simple phenols. C6-Cn compounds—Benzoic acid (n = 1) and derivatives; phenylacetic acid and acetophenones (n = 2); phenylpropanoids, coumarins, phenylalanine, and derivatives (n = 3); naphthoquinones and phenyl butyric acids (n = 4). C6-Cn-C6 compounds—anthraquinones (n = 2); flavonoids (n = 3). Other complex structures—phenolic dimers and hybrids.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Misra, D.; Dutta, W.; Jha, G.; Ray, P. Interactions and Regulatory Functions of Phenolics in Soil-Plant-Climate Nexus. Agronomy 2023, 13, 280. https://doi.org/10.3390/agronomy13020280

AMA Style

Misra D, Dutta W, Jha G, Ray P. Interactions and Regulatory Functions of Phenolics in Soil-Plant-Climate Nexus. Agronomy. 2023; 13(2):280. https://doi.org/10.3390/agronomy13020280

Chicago/Turabian Style

Misra, Deblina, Writuparna Dutta, Gaurav Jha, and Puja Ray. 2023. "Interactions and Regulatory Functions of Phenolics in Soil-Plant-Climate Nexus" Agronomy 13, no. 2: 280. https://doi.org/10.3390/agronomy13020280

APA Style

Misra, D., Dutta, W., Jha, G., & Ray, P. (2023). Interactions and Regulatory Functions of Phenolics in Soil-Plant-Climate Nexus. Agronomy, 13(2), 280. https://doi.org/10.3390/agronomy13020280

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop