THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS

The review article discusses the main issues of creating and using modern chelated microfertilizers based on trace elements in agricultural production. Issues of the role of microelements in the vital activity of living organisms and methods of overcoming the lack of micro­elements in plants are hig...

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Date:2023
Main Author: Trunova, Olena
Format: Article
Language:English
Published: V.I.Vernadsky Institute of General and Inorganic Chemistry 2023
Online Access:https://ucj.org.ua/index.php/journal/article/view/505
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Journal Title:Ukrainian Chemistry Journal
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Ukrainian Chemistry Journal
_version_ 1871465890016395264
author Trunova, Olena
author_facet Trunova, Olena
author_institution_txt_mv [ { "author": "Olena Trunova", "institution": "V.I. Vernadsky Institute of General and Inorganic Chemistry NAS of Ukraine" } ]
author_sort Trunova, Olena
baseUrl_str https://ucj.org.ua/index.php/journal/oai
collection OJS
datestamp_date 2026-07-22T08:23:50Z
description The review article discusses the main issues of creating and using modern chelated microfertilizers based on trace elements in agricultural production. Issues of the role of microelements in the vital activity of living organisms and methods of overcoming the lack of micro­elements in plants are highlighted. An overview of coordination compounds of 3d-metals (Fe, Mn, Zn, Cu, Co, Ni, Mo) with different classes of complexons, features of their structure and properties is presented. It contains relevant material on the use of microelement complexes for the creation of modern chelated fertilizers. Attention is paid to the use of trace elements complexonates in areas contaminated with radionuclides (137Сs, 90Sr).
doi_str_mv 10.33609/2708-129X.88.12.2022.91-138
first_indexed 2025-09-24T17:43:48Z
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fulltext 91 UDK 541.49: 546.72+ 546.73 + 546.74 + 546.47+ 581.133.8+632.121– 54-386 doi: 10.33609/2708-129X.88.12.2022.91-138 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS. O. K. Trunova* V.I. Vernadsky Institute of General and Inorganic Chemistry of the National Academy of Sciences of Ukraine, 32/34 Academic Palladin ave., 03142 Kyiv, Ukraine *e-mail: trelkon@gmail.com The review article discusses the main issues of creating and using modern chelated micro­ fertilizers based on trace elements in agricultural production. Issues of the role of microele­ ments in the vital activity of living organisms and methods of overcoming the lack of micro­ elements in plants are highlighted. An overview of coordination compounds of 3d-metals (Fe, Mn, Zn, Cu, Co, Ni, Mo) with different classes of complexons, features of their structure and properties is presented. It contains relevant material on the use of microelement complexes for the creation of modern chelated fertilizers. Attention is paid to the use of trace elements complexonates in areas contaminated with radionuclides (137Сs, 90Sr). Keywords: coordination compounds, microelements, chelates, complexones, fertilizers, plants. INTRODUCTION. It is possible to elimi­ nate pathological phenomena caused by a de­ crease in the level of biometals in plants by in­ troducing trace element additives into the soil in a form that is easily transported and assimi­ lated by living organisms. In recent years, the interest of scientists in the creation of effective and environmentally safe growth regulators has increased: the development of methods of their synthesis, the mechanisms of action and methods of application are being studied. The role of microelements (МЕ) in the life activity of living organisms is well known. Pa­ thology associated with the lack of ions such as iron, zinc, manganese, copper, cobalt, zinc leads to various functional diseases, impaired metabolism, possibly to the death of animals, reducing productivity and crop yields [1–6]. Мicroelements are involved in such important biochemical processes as respiration, photo­ synthesis, protein synthesis, blood formation, protein, carbohydrate and fat metabolism, hu­ mus synthesis. Due to their catalytic action, microelements allow plants to more effectively use the main nutrients – solar energy, water and macroelements - nitrogen (N), phosphorus (P) 92 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY and potassium (K), which, in turn, has a po­ sitive effect on plant productivity and harvest quality. Microelements are able to strengthen the ability of plant tissues to recover, which significantly reduces damage to plants by di­ seases. Most trace elements are active catalysts of biochemical processes in plants. In addition, trace elements affect the direction of biochem­ ical reactions in plants due to their influence on plant biocolloids. Microelements cannot be replaced by other substances and their de­ ficiency must be filled taking into account the form in which they will be in the soil. Plants can use trace elements only in water-soluble form (mobile form of trace element), and the immobile form can be used by the plant after complex biochemical processes involving soil humic acids. The main role of trace elements in increas­ ing the quality and quantity of the crop is as follows: 1. In the presence of the required amount of trace elements, plants have the ability to synthesize a full range of enzymes, which will allow more intensive use of energy, water and nutrition (N, P, K) and, accordingly, to obtain a higher yield. 2. Microelements and enzymes based on them strengthen the regenerative activity of tissues and prevent plant diseases. 3. Microelements are one of the few sub­ stances that increase plant immunity. Their lack creates a state of physiological depression and general susceptibility of plants to parasitic diseases. That is why today there is a need to create and use new environmentally friendly effective trace element compounds, both in plant and animal production, which are lacking in soils and rations, in order to increase plant yields, improve animal productivity and the quality of plant products . Therefore, the creation of new non-toxic and effective drugs that contribute to the successful resolution of urgent issues in some sectors of agriculture is an important task for agro-industrial complexes around the world. BIOLOGICAL ROLE OF METALS. The most important microelements in plant life are iron, copper, zinc, manganese, magnesium, cobalt, molybdenum, which, according to their im­ portance in living organisms, can be placed in the order Fe>Mn>Zn>Cu>Со>Ni>Cr>V>Mo. Boron, magnesium, calcium are classified as mesoelements, since for the life activity of plants, they are required in much more amounts than microelements. The physiological significance of the main trace elements for plants is given in Table 1. Iron plays a leading role among all me­ tals contained in plants. Organic compounds, which include iron, are necessary in biochemi­ cal processes that occur during respiration and photosynthesis, which is explained by a very high degree of their catalytic properties. The catalytic effect of iron is related to its ability to change the degree of oxidation. The іron ion is oxidized and reduced relatively easily, there­ fore iron compounds are carriers of electrons in biochemical processes. The process of elec­ tron transfer is the basis of the reactions that occur during plant respiration. This process is carried out by enzymes – dehydrogenases and cytochromes containing iron. Among other processes, the influence on the formation of the structure and functioning of chloroplasts, as well as the synthesis of chlorophyll, should also be noted [7]. 93https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Table 1. Physiological significance of the main microelements in plants. МЕ Functions in plants Symptoms of deficiency and its consequences Plants prone to deficiency Fe • A necessary component of many enzymes in plants. • Is contained in chloroplasts and takes part in the photosynthesis and metabolism of N and S. • The main component in the synthesis of chlorophyll. • Can stimulate chlorosis, which appears on young leaves due to low mobility of Fe in the plant. • In cereals, chlorosis manifests itself in the form of interspersed yellow and green stripes along the leaf. • Fe deficiency often causes shoot dieback. Citrus, fruit trees, vineyards, legumes, corn, tomatoes, ros­ es and ornamental plants Mn • necessary for normal photosynthe­ sis, • participates in the reduction of CO2, • plays a role in maintaining the structure of chloroplasts. • partici­ pates in the synthesis of vitamin C • Violation of the ratio of elements of natu­ ral nutrition, • occurrence of point chlorosis, • sometimes complete absence of fruiting Оats, barley, beets, beans, tomatoes, ap­ ple trees, roses Zn • Catalyst in many enzyme systems. • As part of enzymes, it participates in the metabolism of starch and nit­ rogen. • Metabolism of carbohydrates, phos­ phates and proteins; formation of growth hormones auxins, DNA, ri­ bosomes. • growth retardation - shredding • short internodes • interveinal chlorosis • brown spots on upper leaves • deformed leaves and fruits Corn, hops, beans, flax, green vegetables, citrus fruits, grapes, apples and pears Cu • Mainly in the composition of pro­ teins in green cells, responsible for binding solar energy. • Along with Zn, activates an enzyme that prevents the destruction of plant cells. • Par­ ticipates in the process of protein and carbohydrate metabolism • Chlorosis and curling of leaves due to dying of their tips. • Weakened ovary in cereals - drop in yield in the absence of visible signs of deficiency. • Reduced release of pollen grains, which leads to less pollination of flo­ wers and reduced yield. It causes "hanging" of tree crown branches and laying of cereals (low yield). Cereals, citrus fruits, apple trees, pears, green vegetables, rice, alfalfa. Co •A component of vitamin B12, neces­ sary for nitrogen fixation in plants • increases the intensity of respiration and photosynthesis, contributing to the formation of chlorophyll and re­ ducing its decay in the dark • Poor growth can be corrected by using am­ monium and nitrate nitrogen. • Manifestation of chlorosis on the leaves. • Slow plant growth • Development cycle lags behind the norm. Beans, peas, clover, alfalfa Мо •Provides plants with nitrogen • participates in hydrocarbon ex­ change, in the exchange of phospho­ rus fertilizers, in the synthesis of vi­ tamins and chlorophyll, • affects the intensity of redox reactions • the edges of the leaves acquire an orange, red or pink shade • Plant growth is inhibited, leaves are de­ formed and die prematurely. • nitrates accumulate and nitrogen metabo­ lism is disturbed - the content of ascorbic acid decreases. • violations of the phosphorus me­ tabolism of plants are observed. soybeans, grain and leguminous crops, clover, perennial gra­ sses 94 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY To activate the process of iron up take by the plant, a biochemical adaptation of the pri­ mary metabolism is necessary, which requires primarily changes in energy consumption in the form of macroergic compounds, which are represented in the cell by such basic forms as nicotinamate (NADadenine) dinucleotide phosphate and adenosine triphosphate. In the course of the development of any organism, the most important role in providing cells with these components belongs to mitochondria, since for adaptive reactions, the effect of iron deficiency on these qi organelles is impor­ tant [8]. A high degree of mitochondrial sensitivity in this aspect can be explained by the high need for iron to maintain the activity of metalloen­ zymes, iron-sulfur proteins and cytochromes, thanks to the work of which protons and elec­ trons, ultimately, are transferred to the oxygen in the air. Electron carrier proteins include iron-sulfur proteins (Fig. 1), containing frag­ ments of the (Fe-S)n ferredoxin cluster. In them, iron is tetrahedrally surrounded by sul­ fur atoms of thiolate fragments of cysteine. In addition to cubic clusters of the type [4Fe - 4S], larger ones are also known: [8Fe – 7S] and [Mo-7Fe-8S-X] (in nitrogenase). Fig. 1. – A fragment of the iron-sulfur protein structure (Cys is a cytein residue). Iron is necessary for the synthesis of cyto­ chromes, pyridoxine and other iron-sulfur proteins, components of the reaction centers of the chloroplast photosystem, cytochrome oxi­ dase, catalase, peroxidase and other enzymes that play key roles in the main physiological processes – photosynthesis, respiration, nitro­ gen fixation and metabolism. Iron has a special function – indispensable participation in the biosynthesis of chlorophyll. Therefore, any reason that limits the availabili­ ty of iron for plants leads to serious diseases, in particular to chlorosis. When photosynthesis and respiration are impaired and weakened as a result of the insufficient formation of orga­ nic substances from which the plant's body is built, and the lack of organic reserves, a general metabolic disorder occurs. Therefore, with an acute lack of iron, the death of plants inevitably occurs. In trees and shrubs, the green color of the apical leaves disappears completely, they become almost white, and gradually dry up. Manganese is absorbed by plants and dis­ tributed among their organs as a result of meta­ bolic processes. Passive adsorption takes place, especially at high and toxic levels of its content in the solution. Manganese is distinguished by a high degree of absorption activity and rapid transfer in plants. In plant fluids and extracts, it is present in the form of free cationic forms and is transported in plants in the form of Mn2+, and its significant concentrations are found in young plant organs. One of the most important functions of manganese is participation in redox reactions. Mn2+ is a component of two enzymes: phosphotransferase and arginase. In addition, it can replace magnesium in other enzymes and increases the activity of some oxidases. The lat­ ter happens, apparently, as a result of a change in the valence of manganese. 3 metabolism yield). Co •A component of vitamin B12, necessary for nitrogen fixation in plants • increases the intensity of respiration and photosynthesis, contributing to the formation of chlorophyll and reducing its decay in the dark •Poor growth can be corrected by using ammonium and nitrate nitrogen. • Manifestation of chlorosis on the leaves. •Slow plant growth • Development cycle lags behind the norm. Beans, peas, clover, alfalfa Мо •Provides plants with nitrogen • participates in hydrocarbon exchange, in the exchange of phosphorus fertilizers, in the synthesis of vitamins and chlorophyll, • affects the intensity of redox reactions • the edges of the leaves acquire an orange, red or pink shade • Plant growth is inhibited, leaves are deformed and die prematurely. • nitrates accumulate and nitrogen metabolism is disturbed - the content of ascorbic acid decreases. • violations of the phosphorus metabolism of plants are observed. soybeans, grain and leguminous crops, clover, perennial grasses To activate the process of iron up take by the plant, a biochemical adaptation of the primary metabolism is necessary, which requires primarily changes in energy consumption in the form of macroergic compounds, which are represented in the cell by such basic forms as nicotinamate (NADadenine) dinucleotide phosphate and adenosine triphosphate. In the course of the development of any organism, the most important role in providing cells with these components belongs to mitochondria, since for adaptive reactions, the effect of iron deficiency on these qi organelles is important[8]. A high degree of mitochondrial sensitivity in this aspect can be explained by the high need for iron to maintain the activity of metalloenzymes, iron-sulfur proteins and cytochromes, thanks to the work of which protons and electrons, ultimately, are transferred to the oxygen in the air. Electron carrier proteins include iron-sulfur proteins (Fig. 1), containing fragments of the (Fe-S)n ferredoxin cluster. In them, iron is tetrahedrally surrounded by sulfur atoms of thiolate fragments of cysteine. In addition to cubic clusters of the type [4Fe - 4S], larger ones are also known: [8Fe – 7S] and [Mo-7Fe-8S-X] (in nitrogenase). Fig. 1. – A fragment of the iron-sulfur protein structure (Cys is a cytein residue). Iron is necessary for the synthesis of cytochromes, pyridoxine and other iron-sulfur proteins, components of the reaction centers of the chloroplast photosystem, cytochrome oxidase, catalase, peroxidase and other enzymes that play key roles in the main physiological processes – photosynthesis, respiration, nitrogen fixation and metabolism. Iron has a special function – indispensable participation in the biosynthesis of chlorophyll. Therefore, any reason that limits the availability of iron for plants leads to serious diseases, in particular to chlorosis. When photosynthesis and respiration are impaired and weakened as a result of the insufficient formation of organic substances from which the plant's body is built, 95https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Manganese is necessary for normal photo­ synthesis, participates in the reduction of CO2, plays a role in maintaining the structure of chloroplasts. In the absence of manganese, chlorophyll quickly breaks down in the light. Manganese activates more than 35 enzymes involved in various reactions, including nitro­ gen metabolism. Owing to this, it is difficult for plants experiencing a lack of manganese to use nitrates as a source of nitrogen nutrition. In ad­ dition, manganese participates in the synthesis of vitamin C, other vitamins and sugars, regu­ lates the water regime, increases resistance to adverse factors, affects fruiting and promotes the acceleration of fruit development. The lack of manganese greatly affects the in­ tensity of photosynthesis in plants. For exam­ ple, in oats with a lack of manganese, the inten­ sity of photosynthesis drops by about 2 times. Manganese takes an active part in the release of oxygen during photosynthesis and water split­ ting. Also, in the absence of manganese, chloro­ phyll is quickly destroyed in the light. Violation of the photosynthesis system leads to a sharp decrease in the carbohydrate content of the plant, especially in the root part, so the lack of manganese is a key factor in the slowing down of the growth of the root system in plants. Signs of manganese deficiency in plants most often appear on carbonate soils, on cher­ nozems rich in humus, and on soils with a soil solution pH close to neutral. The highest con­ centration of manganese is observed in acidic soils, where pH is below 6.5. This feature is ex­ plained by the fact that with a decrease in pH by 1.0, the content of mobile manganese in the soil increases by a factor of 10, i.e. liming reduc­ es the content of mobile manganese in the soil, and the use of acidic fertilizers, on the cont­ rary, contributes to its increase. Manganese deficiency is exacerbated at low temperatures and high humidity, so winter and perennial crops are sensitive to its deficiency in spring. The introduction of sulfur, superphosphates (substances that acidify the soil) into the soil increases the content of available manganese. The lack of manganese in the soil is especially acutely felt by cereals, in particular oats, as well as corn, legumes, beets, potatoes, rapeseed, peas, green crops (dill, parsley, spinach, onion, horseradish) apple, cherry, raspberry, grapes [9]. An external sign of manganese deficiency is leaf spot and necrosis. Zinc has a great influence on oxidation-re­ duction processes, the rate of which is signifi­ cantly reduced when it is lacking. Zinc defi­ ciency leads to disruption of hydrocarbon con­ version processes. It has been established that with a lack of zinc in the leaves and roots of to­ matoes, citrus fruits and other crops, phenol­ ic compounds, phytosterols or lecithins accu­ mulate, and the starch content decreases. The importance of zinc for plant growth is closely related to its participation in nitrogen metabo­ lism. Zinc deficiency leads to a significant ac­ cumulation of soluble nitrogen compounds – amines and amino acids, which disrupts pro­ tein synthesis. Many studies have confirmed that the protein content of plants decreases with zinc deficiency. Zinc is part of various enzymes: carbonic an­ hydrase, triose phosphate dehydrogenase, per­ oxidase, oxidase, polyphenol oxidase, etc. The importance of zinc for plant growth is closely related to its participation in nitrogen metabo­ lism. Zinc deficiency leads to significant ac­ cumulation of soluble nitrogen compounds – amines and amino acids, which disrupts pro­ tein synthesis. Many studies have confirmed that the protein content of plants decreases 96 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY with a lack of zinc. Under the influence of zinc, the synthesis of sucrose, starch, the total con­ tent of carbohydrates and protein substances increase. The use of zinc fertilizers increases the content of ascorbic acid, dry matter and chlorophyll. Zinc fertilizers increase drought, heat and cold resistance of plants [10]. Zn2+ ions form complexes with ligands with donor O and N atoms. Zinc is part of the active center of many important enzymes, mainly catalyzing reactions of hydrolysis of peptides, collagen, phospholipids, etc. Zinc activates carbonichy­ drase enzyme (Fig. 2), which is responsible for the hydration of CO2 in biofluids and the transfer of H+ ions to СО3 2-, which regulates one of the most important buffer systems of the body. Zinc-containing enzymes form of «zinc fingers» wonderful shape. This happens because DNA fragments form repetitive do­ mains, which «fold» near zinc ions and cha- racteristic folds – «fingers» appear. The "fingers" include fragments of the type (Cys)2(His)2, (Cys)3(His), (Cys)4 or thiolate cluster complex­ es with bridging cysteine residues. a b Fig. 2 – Carbonichydrase (a) and a fragment of xanthineoxidase (b). 5 a b Fig. 2 – Carbonichydrase (a) and a fragment of xanthineoxidase (b). Zinc is part of various enzymes: carbonic anhydrase, triose phosphate dehydrogenase, peroxidase, oxidase, polyphenol oxidase, etc. The importance of zinc for plant growth is closely related to its participation in nitrogen metabolism. Zinc deficiency leads to significant accumulation of soluble nitrogen compounds – amines and amino acids, which disrupts protein synthesis. Many studies have confirmed that the protein content of plants decreases with a lack of zinc. Under the influence of zinc, the synthesis of sucrose, starch, the total content of carbohydrates and protein substances increase. The use of zinc fertilizers increases the content of ascorbic acid, dry matter and chlorophyll. Zinc fertilizers increase drought, heat and cold resistance of plants [10]. Zn2+ ions form complexes with ligands with donor O and N atoms. Zinc is part of the active center of many important enzymes, mainly catalyzing reactions of hydrolysis of peptides, collagen, phospholipids, etc. Zinc activates carbonichydrase enzyme (Fig. 2), which is responsible for the hydration of CO2 in biofluids and the transfer of H+ ions to СО32-, which regulates one of the most important buffer systems of the body. Zinc-containing enzymes form of «zinc fingers» wonderful shape. This happens because DNA fragments form repetitive domains, which «fold» near zinc ions and characteristic folds – «fingers» appear. The "fingers" include fragments of the type (Cys)2(His)2, (Cys)3(His), (Cys)4 or thiolate cluster complexes with bridging cysteine residues. All cultivated plants in relation to zinc are divided into 3 groups: very sensitive (corn, flax, hops, grapes, fruits); moderately sensitive (soy, haricot bean, fodder legumes, peas, sugar beets, sunflower, clover, onions, potatoes, cabbage, cucumbers, berries); slightly sensitive (oats, wheat, barley, rye, carrots, rice, alfalfa). Zinc deficiency has the strongest effect on the formation of seeds than on the development of vegetative organs. Symptoms of zinc deficiency are widely found in various fruit crops (apple, cherry, Japanese plum, walnut, pecan, apricot, avocado, lemon, grape). Citrus crops especially suffer from the lack of zinc. With zinc deficiency, chlorotic spots appear on the leaves of plants, which become pale green, and in some plants they are almost white. In apple, pear, and walnut trees, zinc deficiency develops the so-called rosette disease, which is expressed in the formation of small leaves at the ends of branches, which are arranged in the form of a rosette [11]. With zinc starvation, few fruit buds are laid. The grain yield drops sharply. Among field crops, zinc deficiency most often manifests itself in corn in the form of a white sprout or a white tip. An indicator of zinc starvation in legumes (haricot bean, soybeans) is the presence of chlorosis on leaves, sometimes asymmetric development of the leaf blade. The lack of zinc for 5 a b Fig. 2 – Carbonichydrase (a) and a fragment of xanthineoxidase (b). Zinc is part of various enzymes: carbonic anhydrase, triose phosphate dehydrogenase, peroxidase, oxidase, polyphenol oxidase, etc. The importance of zinc for plant growth is closely related to its participation in nitrogen metabolism. Zinc deficiency leads to significant accumulation of soluble nitrogen compounds – amines and amino acids, which disrupts protein synthesis. Many studies have confirmed that the protein content of plants decreases with a lack of zinc. Under the influence of zinc, the synthesis of sucrose, starch, the total content of carbohydrates and protein substances increase. The use of zinc fertilizers increases the content of ascorbic acid, dry matter and chlorophyll. Zinc fertilizers increase drought, heat and cold resistance of plants [10]. Zn2+ ions form complexes with ligands with donor O and N atoms. Zinc is part of the active center of many important enzymes, mainly catalyzing reactions of hydrolysis of peptides, collagen, phospholipids, etc. Zinc activates carbonichydrase enzyme (Fig. 2), which is responsible for the hydration of CO2 in biofluids and the transfer of H+ ions to СО32-, which regulates one of the most important buffer systems of the body. Zinc-containing enzymes form of «zinc fingers» wonderful shape. This happens because DNA fragments form repetitive domains, which «fold» near zinc ions and characteristic folds – «fingers» appear. The "fingers" include fragments of the type (Cys)2(His)2, (Cys)3(His), (Cys)4 or thiolate cluster complexes with bridging cysteine residues. All cultivated plants in relation to zinc are divided into 3 groups: very sensitive (corn, flax, hops, grapes, fruits); moderately sensitive (soy, haricot bean, fodder legumes, peas, sugar beets, sunflower, clover, onions, potatoes, cabbage, cucumbers, berries); slightly sensitive (oats, wheat, barley, rye, carrots, rice, alfalfa). Zinc deficiency has the strongest effect on the formation of seeds than on the development of vegetative organs. Symptoms of zinc deficiency are widely found in various fruit crops (apple, cherry, Japanese plum, walnut, pecan, apricot, avocado, lemon, grape). Citrus crops especially suffer from the lack of zinc. With zinc deficiency, chlorotic spots appear on the leaves of plants, which become pale green, and in some plants they are almost white. In apple, pear, and walnut trees, zinc deficiency develops the so-called rosette disease, which is expressed in the formation of small leaves at the ends of branches, which are arranged in the form of a rosette [11]. With zinc starvation, few fruit buds are laid. The grain yield drops sharply. Among field crops, zinc deficiency most often manifests itself in corn in the form of a white sprout or a white tip. An indicator of zinc starvation in legumes (haricot bean, soybeans) is the presence of chlorosis on leaves, sometimes asymmetric development of the leaf blade. The lack of zinc for All cultivated plants in relation to zinc are divided into 3 groups: very sensitive (corn, flax, hops, grapes, fruits); moderately sensitive (soy, haricot bean, fodder legumes, peas, su­ gar beets, sunflower, clover, onions, potatoes, cabbage, cucumbers, berries); slightly sensitive (oats, wheat, barley, rye, carrots, rice, alfalfa). Zinc deficiency has the strongest effect on the formation of seeds than on the develop­ ment of vegetative organs. Symptoms of zinc deficiency are widely found in various fruit crops (apple, cherry, Japanese plum, walnut, pecan, apricot, avocado, lemon, grape). Citrus crops especially suffer from the lack of zinc. With zinc deficiency, chlorotic spots appear on the leaves of plants, which become pale green, and in some plants they are almost white. In apple, pear, and walnut trees, zinc deficiency develops the so-called rosette disease, which is expressed in the formation of small leaves at 97https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 the ends of branches, which are arranged in the form of a rosette [11]. With zinc starvation, few fruit buds are laid. The grain yield drops sharply. Among field crops, zinc deficiency most often manifests itself in corn in the form of a white sprout or a white tip. An indicator of zinc starvation in legumes (haricot bean, soy­ beans) is the presence of chlorosis on leaves, sometimes asymmetric development of the leaf blade. The lack of zinc for plants is most often observed on sandy and sub-sandy soils with a low zinc content, as well as on carbonate and old plowed soils. In plants, cobalt affects the accumulation of nitrogenous substances and carbohydrates, increases the intensity of respiration and pho­ tosynthesis, contributing to the formation of chlorophyll and reducing its decay in the dark. Cobalt also increases the overall water content of plants, especially during droughts, and is absolutely necessary for the growth of nodule bacteria and their nitrogen fixation. In plants, this element is found in ionic form and in the composition of vitamin B12 (about 4.5%). Plants, like animals, do not synthesize vitamin B12. It is produced by the bacteria of nodules of leguminous plants and participates in the synthesis of methionine. It is part of vi­ tamin B12, which is present in the nodules, and has a noticeable positive effect on the activity of enzyme hydrogenase, and also increases the activity of nitrate reductase in the nodules of legume crops. This trace element affects the ac­ cumulation of sugars and fats in plants, has a beneficial effect on the synthesis of chlorophyll in plant leaves, reduces its decay in the dark, increases the intensity of respiration, and the content of ascorbic acid in plants. As a result of foliar fertilization with cobalt in plant leaves, the total content of nucleic acids increases. Co­ balt has a noticeable positive effect on the acti­ vity of enzyme hydrogenase, and also increases the activity of nitrate reductase in the tubers of leguminous crops. Cobalt takes an active part in oxidation and reduction reactions, stimu­ lates the Krebs cycle and has a positive effect on respiration and energy metabolism, as well as protein biosynthesis of nucleic acids. Due to its positive effect on metabolism, protein syn­ thesis, assimilation of carbohydrates, etc. It is a powerful growth stimulator. As already mentioned, cobalt is part of co­ balamin – coenzyme B12 (Fig. 3). Fig. 3 – Cobalamin fragment near the coordi­ nation center. Cobalamin contains a macrocycle – a corrin ring connected to a nucleotide and dimethyl­ benzimidazole. The cavity in the center of the corrin ring is occupied by a Co atom with a coordination number of 5, and the sixth co­ ordination position can be occupied by 5-de­ oxyadenosine, connected to Co through the –СН2– group. Due to this, coenzyme B12 is a rare example of a natural organometallic com­ pound. If the sixth coordination position is oc­ cupied by any other small ligands, aquacobala­ min, hydroxocobalamin, cyanocobalamin are 6 plants is most often observed on sandy and sub-sandy soils with a low zinc content, as well as on carbonate and old plowed soils. In plants, cobalt affects the accumulation of nitrogenous substances and carbohydrates, increases the intensity of respiration and photosynthesis, contributing to the formation of chlorophyll and reducing its decay in the dark. Cobalt also increases the overall water content of plants, especially during droughts, and is absolutely necessary for the growth of nodule bacteria and their nitrogen fixation. In plants, this element is found in ionic form and in the composition of vitamin B12 (about 4.5%). Plants, like animals, do not synthesize vitamin B12. It is produced by the bacteria of nodules of leguminous plants and participates in the synthesis of methionine. It is part of vitamin B12, which is present in the nodules, and has a noticeable positive effect on the activity of enzyme hydrogenase, and also increases the activity of nitrate reductase in the nodules of legume crops. This trace element affects the accumulation of sugars and fats in plants, has a beneficial effect on the synthesis of chlorophyll in plant leaves, reduces its decay in the dark, increases the intensity of respiration, and the content of ascorbic acid in plants. As a result of foliar fertilization with cobalt in plant leaves, the total content of nucleic acids increases. Cobalt has a noticeable positive effect on the activity of enzyme hydrogenase, and also increases the activity of nitrate reductase in the tubers of leguminous crops. Cobalt takes an active part in oxidation and reduction reactions, stimulates the Krebs cycle and has a positive effect on respiration and energy metabolism, as well as protein biosynthesis of nucleic acids. Due to its positive effect on metabolism, protein synthesis, assimilation of carbohydrates, etc. It is a powerful growth stimulator. As already mentioned, cobalt is part of cobalamin - coenzyme B12 (Fig. 3). Fig. 3 – Cobalamin fragment near the coordination center. Cobalamin contains a macrocycle – a corrin ring connected to a nucleotide and dimethylbenzimidazole. The cavity in the center of the corrin ring is occupied by a Co atom with a coordination number of 5, and the sixth coordination position can be occupied by 5- deoxyadenosine, connected to Co through the –СН2– group. Due to this, coenzyme B12 is a rare example of a natural organometallic compound. If the sixth coordination position is occupied by any other small ligands, aquacobalamin, hydroxocobalamin, cyanocobalamin are formed. In cobalamin, the CO atom can be in 3 oxidation states: +3, +2, +1, and all of them are low-spin. The main enzymatic role of cobalamin is related to the exchange transfer of H or CH3 radicals between bioligands. Other cobalamin enzymes catalyze radical exchange in the cases of isomerization (mutase) and dehydration (lyase). Radical exchange begins with the weakening of the Co-C bond, which leads to the formation of low-spin 5-coordinated Co(II) and the CH2R radical, which is replaced by any other radical. CH3 group transfer reactions are based on the high nucleophilicity of the Co+1 ion in a square environment. This reaction takes place during the 98 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY formed. In cobalamin, the CO atom can be in 3 oxidation states: +3, +2, +1, and all of them are low-spin. The main enzymatic role of co­ balamin is related to the exchange transfer of H or CH3 radicals between bioligands. Other co­ balamin enzymes catalyze radical exchange in the cases of isomerization (mutase) and dehyd­ ration (lyase). Radical exchange begins with the weakening of the Co-C bond, which leads to the formation of low-spin 5-coordinated Co(II) and the CH2R radical, which is replaced by any other radical. CH3 group transfer re­ actions are based on the high nucleophilicity of the Co+1 ion in a square environment. This reaction takes place during the biosynthesis of methionine, as well as for the activity of metha­ nogenic bacteria that produce methane. Cobalt has a positive effect on the forma­ tion of nitrogen-fixing nodule bacteria in le­ gumes, improves the growth and development of plants through the interaction of cell hor­ mones during auxin metabolism, participates in redox reactions, photosynthesis (increases the amount of chlorophyll), synthesis of nu­ cleic acids, promotes the intensity of the pas­ sage of respiratory processes, the formation in plants, carbohydrates, fats, sugars, vitamins (ascorbic acid), activates enzymes (in particu­ lar nitrate reductase), accelerates the develop­ ment of vegetative organs, promotes flowering, can accumulate in pollen, forms frost resis­ tance, heat resistance (increases the total water content), increases resistance to stress - factors, diseases, in cereals ( resistance to lodging), in­ creases productivity, improves the quality of grown products, promotes better absorption of nitrogen, potassium, phosphorus, magnesi­ um from the soil and limits the entry of heavy metals into the organs of agricultural plants. Cobalt can move freely from the leaves to other organs of the plant, which is an impor­ tant indicator in foliar feeding [12, 13]. Copper is an essential redox-active transi­ tion metal that is involved in many physiologi­ cal processes in plants because it can exist in multiple oxidation states in vivo. Under phy­ siological conditions Cu exists as Cu2+ and Cu+. Cu acts as a structural element in regulatory proteins and participates in photosynthetic electron transport, mitochondrial respira­ tion, oxidative stress responses, cell wall me­ tabolism and hormone signaling. Cu ions act as cofactors in many enzymes such as Cu/Zn superoxide dismutase (SOD), cytochrome c oxidase, amino oxidase, laccase, plastocyanin and polyphenol oxidase. At the cellular level, Cu also plays an essential role in signaling of transcription and protein trafficking machine­ ry, oxidative phosphorylation and iron mobili­ zation. Thus, plants require Cu as an essential micronutrient for normal growth and deve­ lopment; when this ion is not available plants develop specific deficiency symptoms, most of which affect young leaves and reproductive organs. The redox properties that make Cu an essential element also contribute to its inhe­ rent toxicity. Redox cycling between Cu2+ and Cu+ can catalyze the production of highly toxic hydroxyl radicals, with subsequent damage to DNA, lipids, proteins and other biomolecules. Thus, at high concentrations, Cu can become extremely toxic causing symptoms such as chlorosis and necrosis, stunting, leaf disco­ loration and inhibition of root growth. At the cellular level, toxicity may result from 1) bind­ ing to sulfhydryl groups in proteins, thereby inhibiting enzyme activity or protein function; 2) induction of a deficiency of other essen­ tial ions; 3) impaired cell transport processes; 4) oxidative damage [14, 15]. 99https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 8 enzyme superoxide dismutase, has been studied in the most detail. Oxygen carrier proteins include the protein hemocyanin, which is intracellular, which is generally characteristic of Cu- containing proteins (Fig. 4). b Fig. 4 – Fragment of the structure of copper-containing proteins: hemocyanin (a), plastocyanin (b). In the hemocyanin oligomer, each monomer unit contains 2 copper atoms located very close together. Deoxyhemocyanin is colorless, but acquires a bright blue color when binding O2. In deoxyhemocyanin, the Cu(I) atom has a coordination number of 3 and pyramidally coordinates 3 histidine residues. After the addition of an O2 molecule, 2 bridging bonds are formed, which connect 2 copper atoms. At the same time, O2 is reduced to О22-. The protein residues converge significantly, and the Cu atoms have a coordination number of 5, which is typical only for Cu(II). Electron carriers are the so-called "blue" copper proteins containing both Cu(I) and Cu(II), as well as residues of thiolate groups, imidazole, and cysteine. In plastocyanin and azurin, there is a planar Cu(I) complex with a coordination number of 3. When coordinating the fourth ligand, which usually contains a donor sulfur atom, the coordination number of Cu(I) increases to 4 in a tetrahedral environment. In cytochrome-C-oxidase and N2O-reductase, the center of the enzyme is a binuclear complex in which 2 Cu atoms are connected through a bidentate cysteine residue, and each Cu atom coordinates a heterocyclic imidazole nitrogen atom. In one-electron oxidation of this form, a purple paramagnetic complex is formed, in which the unpaired electrons belong to both copper atoms. Despite the fact that a number of other macro- and microelements greatly affect the rate of redox processes, the effect of copper in these reactions is specific, and it cannot be replaced by any other element. Under the influence of copper, the activity of peroxysylase increases and the activity of synthetic centers decreases and leads to the accumulation of soluble carbohydrates, amino acids and other products of the breakdown of complex organic substances. Copper is a constituent part of a number of the most important oxidizing enzymes – polyphenol oxidase, ascorbin oxidase, lactase, dehydrogenase, etc. All of these enzymes carry out oxidation reactions by transferring electrons from the substrate to molecular oxygen, which is an electron acceptor. In connection with this function, the valence of copper in redox reactions changes from a divalent to a monovalent state and back. Almost all copper in leaves is concentrated in chloroplasts mainly in the form of plastocyanin and is closely related to the processes of photosynthesis: it stabilizes chlorophyll, protecting it from destruction. Copper is part of copper protein, forming an oxidizing enzyme, Plants use Cu as a cofactor for a wide range of proteins involved in several physiological processes, including photosynthesis, mito­ chondrial respiration, carbohydrate metab­ olism, formation of phenolics in response to pathogen attack, superoxide scavenging, cell wall remodeling, and ethylene perception. The majority of Cu proteins (~90%) found in nature function as oxidoreductases. The most abundant Cu protein in plants is plastocyanin (which utilizes about 50% of Cu in plastids), a protein essential for photosynthetic elec­ tron transport in chloroplasts that transfers electrons from the cytochrome b6f complex to photosystem I (PSI). Cu is part of Complex IV of the mitochondrial respiratory chain, and thus is involved in metabolic pathways that supply energy for cellular processes. Other Cu proteins are Cu/Zn superoxide dismutase (dis­ mutation of superoxide), laccase (cell wall re­ modeling), amine oxidase (cell wall and plant tissue differentiation, wound healing, and re­ sponse to pathogens), and polyphenol oxidase (wounding and pathogen response) [16]. In plant organisms, copper is found mainly in the form of copper-containing proteins [17, 18]. There are more than 20 enzymes contain­ ing copper in the active center, most of which are oxidases. Their biological role is related to the processes of hydroxylation, oxidative cata­ lysis, and oxygen transfer. The role of copper in enzyme cytochrome oxidase, which con­ trols the reactions of the О2 → Н2О, О2 → Н2О2 type, as well as the disproportionation reaction О2- → О2- + Оо, which is very important for the body, and takes place with the participation of the enzyme superoxide dismutase, has been studied in the most detail. Oxygen carrier pro­ teins include the protein hemocyanin, which is intracellular, which is generally characteristic of Cu-containing proteins (Fig. 4). In the hemocyanin oligomer, each mono­ mer unit contains 2 copper atoms located very close together. Deoxyhemocyanin is colorless, but acquires a bright blue color when binding O2. In deoxyhemocyanin, the Cu(I) atom has a coordination number of 3 and pyramidally coordinates 3 histidine residues. After the ad­ dition of an O2 molecule, 2 bridging bonds are formed, which connect 2 copper atoms. At the same time, O2 is reduced to О2 2-. The protein residues converge significantly, and the Cu atoms have a coordination number of 5, which is typical only for Cu(II). а b Fig. 4 – Fragment of the structure of copper-containing proteins: hemocyanin (a), plastocyanin (b). 100 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY Electron carriers are the so-called "blue" cop­ per proteins containing both Cu(I) and Cu(II), as well as residues of thiolate groups, imidazole, and cysteine. In plastocyanin and azurin, there is a planar Cu(I) complex with a coordination number of 3. When coordinating the fourth ligand, which usually contains a donor sulfur atom, the coordination number of Cu(I) in­ creases to 4 in a tetrahedral environment. In cytochrome-C-oxidase and N2O-reduc­ tase, the center of the enzyme is a binuclear complex in which 2 Cu atoms are connected through a bidentate cysteine residue, and each Cu atom coordinates a heterocyclic imidazole nitrogen atom. In one-electron oxidation of this form, a purple paramagnetic complex is formed, in which the unpaired electrons be­ long to both copper atoms. Despite the fact that a number of other macro- and microele­ ments greatly affect the rate of redox processes, the effect of copper in these reactions is spe­ cific, and it cannot be replaced by any other element. Under the influence of copper, the activity of peroxysylase increases and the ac­ tivity of synthetic centers decreases and leads to the accumulation of soluble carbohydrates, amino acids and other products of the break­ down of complex organic substances. Copper is a constituent part of a number of the most important oxidizing enzymes – polyphenol oxidase, ascorbin oxidase, lactase, dehydroge­ nase, etc. All of these enzymes carry out oxi­ dation reactions by transferring electrons from the substrate to molecular oxygen, which is an electron acceptor. In connection with this function, the valence of copper in redox reac­ tions changes from a divalent to a monovalent state and back. Almost all copper in leaves is concentrated in chloroplasts mainly in the form of plastocy­ anin and is closely related to the processes of photosynthesis: it stabilizes chlorophyll, pro­ tecting it from destruction. Copper is part of copper protein, forming an oxidizing enzyme, and promotes the synthesis of iron-contain­ ing enzymes in plants. It positively affects the synthesis of proteins in plants, which ensure the ability of plant tissues to retain water, as a result, copper in the form of fertilizer adds drought and frost resistance to plants and pro­ tection against bacterial and fungal diseases. Copper participates in the process of nitrogen fixation by plants, increases resistance to lodg­ ing. In practice, copper is used in crop produc­ tion, especially on poor peat-swamp soils. With its deficiency, young leaves quickly wither and dry without visible signs of chlorosis, abnormal intense shedding is often observed. [19]. When feeding with ammonia nitrogen, the lack of copper delays the incorporation of ni­ trogen into protein, peptones, and peptides already in the first hours after nitrogen fertili­ zation. This indicates a particularly important role of copper in the application of ammonia nitrogen. A characteristic feature of the action of copper is that this trace element increases the resistance of plants against fungal and bacterial diseases. Copper reduces grain crops diseases of various types of smut, increases the resis­ tance of plants to brown spot, etc. Symptoms of plant diseases with a lack of copper in the soil are manifested for cereals in the whitening and drying of the tips of the leaf blade. With a strong lack of copper, the plants begin to bush intensively, but later earing does not occur, and the entire stem gradually dries up. Fruit crops with a lack of copper suffer from the so-called dry top or exanthema. At the same time, pro­ nounced chlorosis develops between the veins on the leaf blades of plum and apricot trees. In 101https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 tomatoes, when there is a lack of copper, the growth of shoots slows down, the development of roots is weak, the appearance of dark blu­ ish-green leaves and their twisting, the absence of flower formation. Copper deficiency nega­ tively affects plant reproduction. Pollen grains are formed in smaller quantities, and for cereals, an empty ear grain is characteristic. [15, 20]. Thus, summarizing the need and behavior of Cu in plants, the following conclusions can be drawn: 1. Cu is mainly complexed with organic compounds of low molecular weight and with proteins. 2. Cu is found in compounds that do not have conducting functions, as well as in en­ zymes that have vital functions in plant meta­ bolism. 3. Cu plays an important role in several physiological processes – photosynthesis, res­ piration, carbohydrate distribution, reduction and fixation of N, protein exchange and cell wall metabolism. 4. Cu affects the water permeability of xy­ lem vessels and thus controls water relations. 5. Cu controls the production of DNA and RNA, and its deficiency significantly inhibits plant reproduction (reduction of seed produc­ tion, pollen sterility). 6. Cu is involved in disease resistance me­ chanisms. This resistance of plants to fungal diseases is likely to be associated with an ade­ quate supply of Cu. There is also evidence that Cu-enriched plants are susceptible to some diseases. These phenomena may indicate an indirect effect of Cu on plant disease resistance. Currently, molybdenum has been put for­ ward in one of the first places among other microelements in terms of its practical impor­ tance, since this element turned out to be a very important factor in solving one of the cardinal problems of modern agriculture – providing plants with nitrogen. With a lack of molybde­ num, a large amount of nitrates accumulates in plant tissues and the normal nitrogen me­ tabolism is disturbed [21]. Molybdenum is an essential component in two enzymes that con­ vert nitrate into nitrite (a toxic form of nitro­ gen) and then into ammonia before it is used to synthesize amino acids within the plant. It also needed by symbiotic nitrogen fixing bacteria in legumes to fix atmospheric nitrogen. Mo is involved in hydrocarbon exchange, in the ex­ change of phosphorus fertilizers, in the synthe­ sis of vitamins and chlorophyll, and affects the intensity of redox reactions. After seed treat­ ment with molybdenum, the content of chlo­ rophyll, carotene, phosphorus and nitrogen in the leaves increases. It was established that molybdenum is part of the enzyme nitrate re­ ductase, which restores nitrates in plants. The activity of this enzyme depends on the level of supply of plants with molybdenum, as well as on the forms of nitrogen used for their nutri­ tion. With a lack of molybdenum in the nutri­ ent medium, the activity of nitrate reductase is sharply reduced [22, 23]. Molybdenum is able to detect both different oxidation states (+4, +5, +6) and variable co­ ordination numbers (4, 5, 6, 8). Therefore, the biological action of Mo is diverse. It is the pre­ sence of Mo that allows leguminous plants to assimilate atmospheric nitrogen, in the body of animals, Mo is part of redox enzymes, in­ cluding xanthine oxidase, which is involved in the exchange of purines and the transfer of O2. With an excess of Mo in the soil, it accumulates in the body, which contributes to the activation of xanthine oxidase (Fig. 5) and the synthesis of an excessive amount of uric acid. 102 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY Fig. 5 – Fragment of xanthine oxidase. Like most metals required for plant growth, molybdenum is used by special plant enzymes to participate in reduction and oxidation re­ actions. Molybdenum is an integral part of an organic pterin complex called molybdenum cofactor (Moco). The coordination unit of a Mo-containing enzyme is usually formed from thiolate ligands (for example, pterin), cysteine residues and is supplemented with ligands with donor oxygen atoms: water molecules, OH- and O2- groups. Moco binds to molybde­ num-requiring enzymes (molybdoenzymes) found in most biological systems, including plants. When plants are grown under molyb­ denum deficiency, a number of varied phe­ notypes develop, which hinder plant growth. Most of these phenotypes are associated with reduced activity of molybdoenzymes. These enzymes include primary nitrogen assimila­ tion enzymes, such as nitrate reductase (NR), and nitrogen-fixing enzyme nitrogenase found in bacteroids of legume nodules. Other mo­ lybdoenzymes have also been identified in plants, including xanthine dehydrogenase/oxi­ dase involved in purine catabolism and urei­ de biosynthesis in legumes, aldehyde oxidase (AO), which is involved in ABA biosynthesis, and sulfite oxidase, which can convert sulfite to sulfate, an important step in the catabo­ lism of sulfur-containing amino acids [22–24]. The value of molybdenum in the life of plants is quite diverse. It activates atmospheric nitrogen binding processes of nodule bacteria, promotes the synthesis and exchange of pro­ tein substances in plants. The most sensitive to molybdenum deficiency are such crops as soybeans, grain legumes, clover, and perennial grasses. Plant's need for molybdenum fertili­ zers usually increases on acidic soils with a pH below 5.2. The physiological role of molybde­ num is related to the fixation of atmospheric nitrogen, the reduction of nitrate nitrogen in plants, participation in redox processes, carbo­ hydrate metabolism, and the synthesis of chlo­ rophyll and vitamins. Nitrate reductase with the participation of molybdenum catalyzes the reduction of nitrates and nitrites, and nitrite reductase also with the participation of mo­ lybdenum reduces nitrates to ammonia. This explains the positive effect of molybdenum on increasing the protein content of plants. Under the influence of molybdenum, the content of carbohydrates, carotene and ascorbic acid also increases in plants, and the content of protein substances increases. Under the influence of molybdenum, the content of chlorophyll in plants increases, and the intensity of photosyn­ thesis increases. 10 with molybdenum, as well as on the forms of nitrogen used for their nutrition. With a lack of molybdenum in the nutrient medium, the activity of nitrate reductase is sharply reduced [22, 23]. Molybdenum is able to detect both different oxidation states (+4, +5, +6) and variable coordination numbers (4, 5, 6, 8). Therefore, the biological action of Mo is diverse. It is the presence of Mo that allows leguminous plants to assimilate atmospheric nitrogen, in the body of animals, Mo is part of redox enzymes, including xanthine oxidase, which is involved in the exchange of purines and the transfer of O2. With an excess of Mo in the soil, it accumulates in the body, which contributes to the activation of xanthine oxidase (Fig. 5) and the synthesis of an excessive amount of uric acid. Fig. 5 – Fragment of xanthine oxidase. Like most metals required for plant growth, molybdenum is used by special plant enzymes to participate in reduction and oxidation reactions. Molybdenum is an integral part of an organic pterin complex called molybdenum cofactor (Moco). The coordination unit of a Mo-containing enzyme is usually formed from thiolate ligands (for example, pterin), cysteine residues and is supplemented with ligands with donor oxygen atoms: water molecules, OH- and O2- groups. Moco binds to molybdenum-requiring enzymes (molybdoenzymes) found in most biological systems, including plants. When plants are grown under molybdenum deficiency, a number of varied phenotypes develop, which hinder plant growth. Most of these phenotypes are associated with reduced activity of molybdoenzymes. These enzymes include primary nitrogen assimilation enzymes, such as nitrate reductase (NR), and nitrogen-fixing enzyme nitrogenase found in bacteroids of legume nodules. Other molybdoenzymes have also been identified in plants, including xanthine dehydrogenase/oxidase involved in purine catabolism and ureide biosynthesis in legumes, aldehyde oxidase (AO), which is involved in ABA biosynthesis, and sulfite oxidase, which can convert sulfite to sulfate, an important step in the catabolism of sulfur-containing amino acids [22–24]. The value of molybdenum in the life of plants is quite diverse. It activates atmospheric nitrogen binding processes of nodule bacteria, promotes the synthesis and exchange of protein substances in plants. The most sensitive to molybdenum deficiency are such crops as soybeans, grain legumes, clover, and perennial grasses. Plant's need for molybdenum fertilizers usually increases on acidic soils with a pH below 5.2. The physiological role of molybdenum is related to the fixation of atmospheric nitrogen, the reduction of nitrate nitrogen in plants, participation in redox processes, carbohydrate metabolism, and the synthesis of chlorophyll and vitamins. Nitrate reductase with the participation of molybdenum catalyzes the reduction of nitrates and nitrites, and nitrite reductase also with the participation of molybdenum reduces nitrates to ammonia. This explains the positive effect of molybdenum on increasing the protein content of plants. Under the influence of molybdenum, the content of carbohydrates, carotene and ascorbic acid also increases in plants, and the content of protein substances increases. Under the influence of molybdenum, the content of chlorophyll in plants increases, and the intensity of photosynthesis increases. 103https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 The availability of molybdenum for plant growth strongly depends on soil pH, concen­ tration of adsorbing oxides (e.g., Fe oxides), degree of drainage of water and organic com­ pounds contained in soil colloids. In alkaline soils, molybdenum becomes more soluble and available to plants mainly in anion form. On the contrary, in acidic soils (pH<5.5), the availability of molybdenum decreases, as the adsorption of anions by soil oxides increases [25]. When plants are grown under the con­ ditions of molybdenum deficiency, a number of different phenotypes develop, which inhibit plant growth. Most of these phenotypes are as­ sociated with the reduced activity of molybdo­ enzymes. The lack of molybdenum in plants is mani­ fested in the bright green color of the leaves, while the leaves themselves become narrow, their edges curl inward and gradually die, a dot appears, the leaf veins remain light green. The lack of molybdenum manifests itself, first of all, by the appearance of the yellow-green color of leaves, which is a consequence of the weaken­ ing of atmospheric nitrogen fixation, the stems and petioles of plants become reddish-brown. Nickel belongs to conditionally essential ele­ ments. Nickel is a component of some plant enzymes, especially urease, which metabo­ lizes urea nitrogen into useable ammonia in the plant. Without nickel, toxic levels of urea can accumulate in tissues; forming necrotic legions on leaf tips. Currently, there is a suf­ ficiently large number of scientific works in which the beneficial effects of Ni compounds on plant growth have been proven [26]. The ele­ ment Ni is considered an indispensable trace element for plants because it acts as an activa­ tor of the urease enzyme. Recent studies have shown that Ni can activate the glyoxalase I isoform, which performs an important step in the degradation of methylglyoxal (MG), a po­ tent cytotoxic compound naturally produced by cellular metabolism. Reduced glutathione (GSH) is consumed and regenerated in the de­ toxification process of MG produced during stress (stress-induced production). [26, 27] investigated the role of Ni in the interrelation between the MG cycle and GSH homeostasis and suggested that Ni may play a key role in the metabolism of plant antioxidants, espe­ cially in stressful situations. Some researchers demonstrated the effect of Ni stimulation on the nitrification and mineralization of nitroge­ nous compounds [28], and in [29] it was estab­ lished that microorganisms that metabolize H2 and urea are highly sensitive to Ni nutrition. It was shown in [30] that water-soluble forms of nickel compounds in small concentrations are easily absorbed by plant roots, which has a positive effect on their development. In [31] it was found that Ni binds to ani­ onic organic complexes in xylem exudates. Although the transport and storage of Ni ap­ pears to be metabolically controlled, this metal is mobile in plants and is likely to accumulate simultaneously in leaves and seeds. It should be noted that Ni is easily and quickly taken up by plants from soils, and until a certain con­ centration of Ni in plant tissue is reached, ad­ sorption is positively correlates with soil Ni concentrations. Nickel is found in soil as a free ion and in complexes with other metal ions (such as Fe). In soils, Ni exists in various states of oxidation, but the predominant and more stable form is Ni2+, which exists in a wide range of pH and re­ dox potentials. The biological effects of Ni are very related to its forms, however, regardless of the chemical form of Ni introduced into the 104 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY soil, Ni was found in plants only in the form of neutral and negative complexes. Ni cations are included in the structure of many enzymes, including glyoxalases, ureases, methyl-CoM reductases, superoxide dismutases, peptide deformalylases, and some hydrogenases [27, 32, 33]. It plays an important role in ureolysis, methane biogenesis, acetogenesis, hydrogen metabolism, as well as in the maintenance of the cellular redox state, tolerance to stress and protection and optimal use of nitrogen [34– 36]. Deficiency of nickel ions in plants causes accumulation of urea and necrotic lesions in plant leaves. At excessive concentrations of nickel in plants, its phytotoxic effect is manifested – photosynthesis and transpiration are inhibited in plant tissues. At the same time, the develop­ ment of roots and metabolism lag behind. The most common symptom of Ni toxicity is Fe-in­ duced chlorosis, in which the foliar Fe level is reduced. Another manifestation of nickel toxicity is the reduction of plant growth and photosynthesis caused by induced oxidative stress, inhibition of nitrogen metabolism and enzymatic activity. Thus, nickel salts play a significant role in the growth and development of plants. The absorption of nickel by plants is achieved either by active transport or by pas­ sive diffusion, depending on the plant species, soil pH, the form of nickel compounds, their concentration, and the availability of other metals. Solubilized nickel compounds can be transported by various cationic transport sys­ tems, such as Fe2+, Mg2+, Cu2+, Zn2+ in the form of chelates with citric acid, histidine, and nico­ tiamine, as well as with various proteins, such as permeases, metallothionein, metallochape­ rones [37–39]. Nickel for plants is an important ultra-mi­ croelement that takes part in biological nit­ rogen fixation. The particular importance of the element lies in the increase of resistance to negative manifestations of the environment, which significantly affects the increase in pro­ ductivity. Nickel is responsible for the hydro­ lysis of urea in the plant body (conversion of urea into ammonium (NH4+), as it is an indis­ pensable component of enzyme urease. Nickel has fungicidal properties due to the fact that it directly affects pathogenic organisms or ac­ tivates the protective properties of the crop. In addition, Ni is the main nutrient for nitro­ gen-fixing bacteria. USAGE OF MICRO ELEMENTS IN CROP GROWING. In total, about 75 chemical ele­ ments of Mendeleev's periodic system were found in plant cells, which are part of enzymes, hormones, vitamins and other biologically active compounds. Each of the elements per­ forms its specific function and ensures the normal growth and development of crops. Microelements («metals of life») are necessary for the construction of enzyme systems (bio­ catalysts) for all plants, and it is impossible to replace them with other macro- or meso-ele­ ments. For normal life, crops need more than 30 trace elements in sufficient quantities, in­ cluding both metals (Cu, Zn, Co, Mo, Mn, etc.) and non-metals (I, Si, Se, Br, F, etc.), which are part of various chemical compounds contained in the soil (Table 2.). When there is a lack of available forms of boron, manganese, copper, molybdenum, and in certain conditions also cobalt, zinc, iodine, vanadium and other microelements in the soil, specific diseases of crops are observed, they give a low and inferior yield. In this case, the use of appropriate microfertilizers eliminates plant diseases and significantly increases the 105https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 yield and quality of crop production. Under the action of microelements, the sugar content of many plants increases, the content of starch or protein, vitamins and fats increases. The resistance of plants to drought, high and low temperatures also increases, their susceptibili­ ty to pests and diseases decreases. The value of trace elements goes far beyond crop produc­ tion, as many animal and human diseases are often associated with a lack of trace elements. Table 2. Physiological need of agricultural crops for trace elements [40]. Crop/trace element B Cu Fe Mn Zn Mo Corn ** ** ** ** *** * Sorghum * ** *** *** *** * Soy * * *** *** ** *** Wheat * *** * *** * * Barley * *** * ** * * Pea * * * *** * ** Sunflower *** ** * ** ** * Sugar beet *** ** ** *** ** ** Rape *** * * *** * *** Flax ** *** * * *** * Tomatoes ** ** ** ** ** * Cucumbers * ** * *** * * Onion *** ** *** ** ** *** White-headed cabbage *** ** * *** ** *** Cauliflower *** ** * ** * *** Carrot *** *** * *** * * Potato ** * * ** ** * Grape *** ** *** *** *** * Apple tree *** ** *** *** *** * *** - key microelement; ** - vital microelement; * - an important microelement A deficiency in the soil of certain trace elements can be detected by the appearance of specific signs in the appearance of plants. However, in the practice of agriculture, one has often to meet with a less acute shortage of trace elements, when clear external signs are not observed, but the growth and development of plants are suppressed and they give low yields. The need for the use of microfertilizers can be de`termined based on the results of a chemi­ cal soil analysis for the content of plant-avai­ lable forms of microelements. With the grea­ test accuracy, the need to apply microfertili­ zers in specific soil and climatic conditions can be judged by the results of field experiments. A higher efficiency of using microfertilizers, as a rule, is observed when plants are well sup­ plied with the main nutrients - nitrogen, phos­ phorus and potassium. At the same time, the introduction of the necessary trace elements 106 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY significantly increases the effect of nitrogen, phosphorus and potassium fertilizers. When microelements are introduced, a better use of nutrients from the soil and mineral fertilizers by plants is ensured. But only a small part of trace elements in the soil solution is in a mobile form, easily ab­ sorbed by plants. Therefore, when filling their lack, the form of compounds (degree of availa­ bility for the plant organism) in which they will be in the soil should be taken into account. Most trace elements are part of enzymes and act as active catalysts that accelerate important biochemical reactions in plants. Insignificant amounts of microelements in combined ac­ tion strengthen their catalytic functions and greatly influence the course of life processes in crops. In addition, they affect the orienta­ tion of biochemical processes. For example, copper protects chlorophyll from destruction and contributes to an almost twofold increase in the doses of nitrogen and phosphorus. Man­ ganese regulates the ratio of divalent and triva­ lent iron in plant cells. Boron and manganese have a positive effect on the recovery of crops after freezing, they contribute to the flow of photosynthesis in them. Microelements are of decisive importance in activating the regene­ rative functions of tissues and resistance of the plant organism to various diseases. They are indispensable in increasing the immunity of plants and reducing their susceptibility to parasitic diseases. Only the complete supply of plants with all the necessary trace elements al­ lows crops to fully use energy, water and basic nutrients (nitrogen, phosphorus, potassium), and as a result, to form higher yields. Microfertilizers are able to eliminate plant diseases that arose as a result of an incorrect ratio of macroelements (N, P, K) in their nu­ trition. When one or more microelements are insufficiently supplied to plant cells, there is a decrease in the rate and coherence of the phy­ siological processes responsible for the de­ velopment of the plant organism. As a result, plants are not able to realize their genetic po­ tential, the level and quality of their yield are significantly reduced. Therefore, along with the main elements of mineral nutrition, which contain macro- and mesoelements, it is neces­ sary to take care of the introduction of complex fertilizers, which contain all the microelements necessary for crops. The metabolic action and role of each mic­ roelement in plants can be characterized in re­ lation to some basic processes, such as: 1. Absorption and transport inside the plant 2. Enzymatic processes 3. Concentrations and forms of occurrence 4. Deficiency and toxicity 5. Ionic competition and interaction Chemical balance in living organisms is the main condition for their proper growth and development. The interaction of chemi­ cal elements also has a similar importance to deficiency and toxicity in plant physiology. In­ teractions between chemical elements can be both antagonistic and synergistic, and their unbalanced reactions can cause real chemical stress in plants. Antagonism occurs when the combined physiological effect of two or more elements is less than the sum of their inde­ pendent effects, and synergism occurs when the combined effect of these elements is great­ er. These interactions can also relate to the ability of one element to inhibit or stimulate the absorption of other elements in plants. All these reactions are quite variable and can oc­ cur inside cells, inside membrane surfaces, and also in plant roots. 107https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Below are examples of «interaction»of mac­ ro- and microelements in plants [2, 3]. Zinc-phosphorus – a high level of availa­ ble P causes a deficiency of zinc, which may be associated with the formation of insolu­ ble Zn3(PO4)2 in the soil. P-Zn antagonism in roots affects zinc translocation. Zinc-nitrogen – high levels of nitrogen cause a deficiency of zinc due to increased growth rate with a limiting supply of Zn; retention of Zn in the roots due to the formation of a stable N-Zn protein complex. Iron-phosphorus – an excessive amount of P and an increase in the P/Fe ratio inactivates iron. This effect is probably due to the forma­ tion of a slightly soluble Fe-phosphate preci­ pitate, and the plant is able to absorb and re­ tain Fe in a soluble, mobile form, the amount of which decreases with an increase in the con­ centration of P in tissues. Similar phenomena occur with copper-phosphorus imbalance in plants. Molybdenum-sulfur – the absorption of Mo by plants reduces the S content by direct com­ petition between two equivalent anions of the same size; another explanation suggests that the inhibition of Mo utilization in the plant occurs at low Mo levels. Zinc-magnesium – аn increase in the pH of the soil, after the use of MgCO3, causes the in­ teraction of Zn and Mg inside the plant and in the soil. Zinc-iron – the metabolic functioning of Fe in plants is closely related to the balanced supply of Zn, but with excessive addition of Zn there is a noticeable decrease in the concentra­ tion of Fe in plants. Iron-manganese – Fe and Mn are intercon­ nected in their metabolic functions, the effec­ tiveness of one determines the proportional presence of the other. An excess of Mn reduces the availability of Fe, because Mn prevents the transport of Fe from roots to shoots. Iron-molybdenum – two effects of Mo and Fe are proposed - a beneficial and a harmful one. With an excess of Mo, there is a deficien­ cy of Fe due to the formation of Fe-molybdate, which leads to a decrease in the content of Fe in the solid body (roots). On the other hand, at an equivalent level of these elements, Mo in­ creases the absorption of Fe. Copper-iron – іn several crops and mainly citrus fruits, Fe-chlorosis occurs due to a high concentration of Cu in the nutrient solution Copper-molybdenum – the antagonism of Cu and Mo in plants is observed when Cu in­ terferes with the role of Mo in the enzymatic reduction of NO3. As mentioned above, plants can easily use trace elements only in a biologically active wa­ ter-soluble form (mobile form of a microele­ ment), and the immobile form can be used by the plant after complex biochemical processes involving soil humic acids. In the middle of the 20th century, trace elements in crop produc­ tion were mainly used in the form of inorganic salts of trace elements, which were mainly in­ troduced into the soil in significant quantities. Adding them to the soil contributes to their better assimilation and hence to a more effec­ tive effect on the yield of plants. Preparations of this type have a low cost, which attracts the attention of farmers. However, the use of salts of trace elements is appropriate only on acidic and slightly acidic soils. Salts of inorganic acids are poorly soluble, so they are difficult for plants to assimilate. Their excess can cause a toxic reaction and soil salinization. The twen­ ty-first century is the period of the use of more effective preparations of microelements in the 108 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY form of chelated microfertilizers. They are more effective due to the availability of trace elements for plants, and act as dual action drugs. MICROELEMENTS IN CHELATED FORM. Currently, particular attention is given to the role of microelements in living organisms as complexing agents, since most biochemical ob­ jects in plants are in the form of coordination compounds [41–43]. Living organisms prefer compounds of those elements that are capable of forming sufficiently strong but at the same time labile bonds. These bonds should be easi­ ly subjected to both homolytic and heterolytic rupture as well as cyclization. Such organogens are microelements. The microelements must be introduced into the body in an active form, capable of being transported and absorbed. From this point of view, chelate complexes of biometals are promising [2, 44]. In recent decades, the development of nano­ technology has reached its height. Of particu­ lar interest to researchers are nanosystems of a given composition with predicted properties. When used in chemistry, medicine, biotech­ nology, the size of nano particles or nano-sys­ tems is of great importance because it depends on the permeability, activity, solubility and toxicity of nanoparticles [45, 46]. The biocoordination compounds of metals as medical and biological agents form the ba­ sis of modern socially and technologically sig­ nificant innovative developments. Combining metal ions with an organic compound enables the production of supramolecular associates, which are inherently close to the endogenous coordination compounds that exist in the liv­ ing organism and in general in biosystems. They are less toxic than their constituents and usually have a wide range of biological acti­ vity. The attention of the world scientific com­ munity to this area is caused by its intensive development, as well as the achievements of biocoordination, bioorganic, medical chemist­ ry. More and more new complexing ions and ligands are involved in the orbit of biochemical research. disorders of plants. The theory and practice of the experimen­ tal chemistry of biologically active substances are related to the development of fundamen­ tal principles for the creation of effective drugs based on the structure-activity dependence, which, in turn, is associated with the develop­ ment of theoretical methods, as well as the ac­ cumulation of information on the relationship of molecular structure with biological activity. The effectiveness of the influence of the micro­ elements on any living organism quantitatively and directly depends on the form in which the microelements is. The twenty-first century is a period of use of more effective chelate-based microelements They are more effective due to the availabili­ ty of microelements for living organisms and act as dual action drugs. Chelating compounds (chelates) are coordination compounds of metal (microelements ) with a chelating agent (chelant, ligand) of a cyclic nature. Complex­ ons are the most promising chelating agents. Complexones belong to complex amino­ carboxylic (aminophosphonic) acids, which contain several functional groups: carboxylic (–C (O) O–), phosphonic (PO3H2), and amino (NH-) groups. Therefore, thanks to chemical interaction, it is possible to obtain metal-con­ taining compounds in which metal ions will bind to the ligand with the help of electron-do­ nating atoms (oxygen and nitrogen) with the formation of heterocyclic rings (metal-che­ late cycles). 109https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Among the multifunctional complex-form­ ing compounds, polyaminocarboxylate, phos­ phonic, and aminophosphonic complexones are the most promising from a biological point of view for creating microfertilizers [3, 48–50]. In table 3, the most common chelating agents that are currently used to create microfertili­ zers and in fig. 6 structural formulas of some complexions are shown. Almost all microelements form fairly stable complexes with the given ligands, while the form of the complexes strongly depends on the pH of the solution or soil. The most favorable conditions for the formation of complexes are non-alkaline environments (pH ~ 5.5–6.5). In terms of biochemical structure and chemical purity, chelated complexes of micro­ elements are very similar to organometallic compounds synthesized in plant cells (Fig.  7, a, b). Therefore, upon entering a living cell, these substances will be perceived by them not as alien elements, but as «their own», which will ensure their biogenic compatibility and accordingly, high absorption [51–54]. 16 Fig. 6 - Structural formulas of some complexones. Almost all microelements form fairly stable complexes with the given ligands, while the form of the complexes strongly depends on the pH of the solution or soil. The most favorable conditions for the formation of complexes are non-alkaline environments (pH ~ 5.5–6.5). In terms of biochemical structure and chemical purity, chelated complexes of microelements are very similar to organometallic compounds synthesized in plant cells (Fig. 7, a, b). Therefore, upon entering a living cell, these substances will be perceived by them not as alien elements, but as «their own», which will ensure their biogenic compatibility and accordingly, high absorption [51–54]. Table 3. Chelating agents. Abbreviation The name of the complexones Formula EDTA Ethylenediaminetetraacetic acid C10H16O8N2 DTPA Diethylenetriaminepentaacetic acid C14H23O10N3 CDTA Cyclohexane Tetraacetic acid C14H22O8N2 EDDHA Ethylenediamine-Q-hydroxyphenylacetic acid C18H20O6N2 HEDTA Hydroxyethylenediaminetriacetic acid C10H18O7N2 EDDS Ethylenediaminedisuccinic acid C10H16 O8N2 NTA Nitrilotriacetic acid C6H9O6N EGTA Ethyleneglyco-bis(2-aminoethylether)tetraacetic acid C14H24O10N2 HEDP Hydroxyethylenediphosphonic acid C2H8O7P2 NTP Nitrilotrimethylphosphonic acid C3H12NO9P3 EDТP Ethylenediaminetetraphosphonic acid CIT Citric acid C6H8O7 OX Oxalic acid C2H2O4 Fig. 6 - Structural formulas of some complexones. 110 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY Table 3. Chelating agents. Abbreviation The name of the complexones Formula EDTA Ethylenediaminetetraacetic acid C10H16O8N2 DTPA Diethylenetriaminepentaacetic acid C14H23O10N3 CDTA Cyclohexane Tetraacetic acid C14H22O8N2 EDDHA Ethylenediamine-Q-hydroxyphenylacetic acid C18H20O6N2 HEDTA Hydroxyethylenediaminetriacetic acid C10H18O7N2 EDDS Ethylenediaminedisuccinic acid C10H16 O8N2 NTA Nitrilotriacetic acid C6H9O6N EGTA Ethyleneglyco-bis(2-aminoethylether)tetraacetic acid C14H24O10N2 HEDP Hydroxyethylenediphosphonic acid C2H8O7P2 NTP Nitrilotrimethylphosphonic acid C3H12NO9P3 EDТP Ethylenediaminetetraphosphonic acid CIT Citric acid C6H8O7 OX Oxalic acid C2H2O4 17 a b Fig. 7 – General structure (a) and a fragment of molecular structure (b) of transition metal complexes with EDDS [51]. An organic molecule seems to capture metal in a «claw», and when in contact with a plant, the cell membrane recognizes this complex as a substance related to biological structures, and further the metal ion is absorbed by the plant, and the chelant breaks down into simpler substances (Fig. 8) [3, 49, 53]. Fig. 8 – The structure of the chelate of a microelement and the action of a chelated microfertilizer on plant leaf rotation. The complexonates of microelements have a number of valuable properties: they are non-toxic, dissolve well enough in water, have high stability in a wide pH range, and are not destroyed by microorganisms [3, 4, 6]. It is in complexonates that the microelement is transferred into a mobile, biologically active form. The chelate serves to protect the metal ion, prevents it from reacting with the environment and keeps it in a highly soluble form that can be absorbed by plants, even at a pH that naturally leads to their deposition. The difference between the two forms of microelements (inorganic salts and chelates)is as follows: • trace elements in the form of inorganic salts work satisfactorily only in acidic soils (pH up to 6). In soils close to neutral, their effectiveness decreases tenfold. In neutral, weakly alkaline and carbonate soils, inorganic salts cannot retain microelements in a water-soluble form available to plants and their efficiency approaches zero, i.e. they change to poorly soluble forms (hydroxides, carbonates) and become unavailable to plants; • complex ions are stable in all types of soils, and there are no restrictions on soil pH for them; • microelement complexes are much more effective than ordinary salts, and accordingly their consumption is less. This form of microelements can be used, figuratively speaking, in homeopathic doses, that is, as a prophylactic without even taking into account the composition of the soil and without causing any harm to nature [53]. Among the listed chelants, the most stable complexes are formed by polyaminopolycarboxylic acids (EDDS, EDTA, DTPA, CDTA, EDDHA), which have a high specificity for the iron ion Fe3+ at a certain pH. When increasing the pH, the order of stability of 17 a b Fig. 7 – General structure (a) and a fragment of molecular structure (b) of transition metal complexes with EDDS [51]. An organic molecule seems to capture metal in a «claw», and when in contact with a plant, the cell membrane recognizes this complex as a substance related to biological structures, and further the metal ion is absorbed by the plant, and the chelant breaks down into simpler substances (Fig. 8) [3, 49, 53]. Fig. 8 – The structure of the chelate of a microelement and the action of a chelated microfertilizer on plant leaf rotation. The complexonates of microelements have a number of valuable properties: they are non-toxic, dissolve well enough in water, have high stability in a wide pH range, and are not destroyed by microorganisms [3, 4, 6]. It is in complexonates that the microelement is transferred into a mobile, biologically active form. The chelate serves to protect the metal ion, prevents it from reacting with the environment and keeps it in a highly soluble form that can be absorbed by plants, even at a pH that naturally leads to their deposition. The difference between the two forms of microelements (inorganic salts and chelates)is as follows: • trace elements in the form of inorganic salts work satisfactorily only in acidic soils (pH up to 6). In soils close to neutral, their effectiveness decreases tenfold. In neutral, weakly alkaline and carbonate soils, inorganic salts cannot retain microelements in a water-soluble form available to plants and their efficiency approaches zero, i.e. they change to poorly soluble forms (hydroxides, carbonates) and become unavailable to plants; • complex ions are stable in all types of soils, and there are no restrictions on soil pH for them; • microelement complexes are much more effective than ordinary salts, and accordingly their consumption is less. This form of microelements can be used, figuratively speaking, in homeopathic doses, that is, as a prophylactic without even taking into account the composition of the soil and without causing any harm to nature [53]. Among the listed chelants, the most stable complexes are formed by polyaminopolycarboxylic acids (EDDS, EDTA, DTPA, CDTA, EDDHA), which have a high specificity for the iron ion Fe3+ at a certain pH. When increasing the pH, the order of stability of An organic molecule seems to capture metal in a «claw», and when in contact with a plant, the cell membrane recognizes this complex as a substance related to biological structures, and further the metal ion is absorbed by the plant, and the chelant breaks down into simpler sub­ stances (Fig. 8) [3, 49, 53]. a b Fig. 7 – General structure (a) and a fragment of molecular structure (b) of transition metal complexes with EDDS [51]. 111https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Fig. 8 – The structure of the chelate of a microelement and the action of a chelated microfertilizer on plant leaf rotation. 17 a b Fig. 7 – General structure (a) and a fragment of molecular structure (b) of transition metal complexes with EDDS [51]. An organic molecule seems to capture metal in a «claw», and when in contact with a plant, the cell membrane recognizes this complex as a substance related to biological structures, and further the metal ion is absorbed by the plant, and the chelant breaks down into simpler substances (Fig. 8) [3, 49, 53]. Fig. 8 – The structure of the chelate of a microelement and the action of a chelated microfertilizer on plant leaf rotation. The complexonates of microelements have a number of valuable properties: they are non-toxic, dissolve well enough in water, have high stability in a wide pH range, and are not destroyed by microorganisms [3, 4, 6]. It is in complexonates that the microelement is transferred into a mobile, biologically active form. The chelate serves to protect the metal ion, prevents it from reacting with the environment and keeps it in a highly soluble form that can be absorbed by plants, even at a pH that naturally leads to their deposition. The difference between the two forms of microelements (inorganic salts and chelates)is as follows: • trace elements in the form of inorganic salts work satisfactorily only in acidic soils (pH up to 6). In soils close to neutral, their effectiveness decreases tenfold. In neutral, weakly alkaline and carbonate soils, inorganic salts cannot retain microelements in a water-soluble form available to plants and their efficiency approaches zero, i.e. they change to poorly soluble forms (hydroxides, carbonates) and become unavailable to plants; • complex ions are stable in all types of soils, and there are no restrictions on soil pH for them; • microelement complexes are much more effective than ordinary salts, and accordingly their consumption is less. This form of microelements can be used, figuratively speaking, in homeopathic doses, that is, as a prophylactic without even taking into account the composition of the soil and without causing any harm to nature [53]. Among the listed chelants, the most stable complexes are formed by polyaminopolycarboxylic acids (EDDS, EDTA, DTPA, CDTA, EDDHA), which have a high specificity for the iron ion Fe3+ at a certain pH. When increasing the pH, the order of stability of The complexonates of microelements have a number of valuable properties: they are non-toxic, dissolve well enough in water, have high stability in a wide pH range, and are not destroyed by microorganisms [3, 4, 6]. It is in complexonates that the microelement is trans­ ferred into a mobile, biologically active form. The chelate serves to protect the metal ion, prevents it from reacting with the environment and keeps it in a highly soluble form that can be absorbed by plants, even at a pH that natu­ rally leads to their deposition. The difference between the two forms of microelements (inorganic salts and chelates)is as follows: • trace elements in the form of inorganic salts work satisfactorily only in acidic soils (pH up to 6). In soils close to neutral, their effec­ tiveness decreases tenfold. In neutral, weakly alkaline and carbonate soils, inorganic salts cannot retain microelements in a water-solu­ ble form available to plants and their efficien­ cy approaches zero, i.e. they change to poorly soluble forms (hydroxides, carbonates) and be­ come unavailable to plants; • complex ions are stable in all types of soils, and there are no restrictions on soil pH for them; • microelement complexes are much more effective than ordinary salts, and accordingly their consumption is less. This form of micro­ elements can be used, figuratively speaking, in homeopathic doses, that is, as a prophylactic without even taking into account the composi­ tion of the soil and without causing any harm to nature [53]. Among the listed chelants, the most stable complexes are formed by polyaminopolycar­ boxylic acids (EDDS, EDTA, DTPA, CDTA, EDDHA), which have a high specificity for the iron ion Fe3+ at a certain pH. When increas­ ing the pH, the order of stability of the com­ plexes decreases as follows: EDDHA> DTPA> CDTA> EDTA> EDDS (Fig. 9) [3]. It should be noted that EDDHA has a high selectivity for Fe3+ in a wide pH range (from 4 to 9), but, unfortunately, this effective chelant forms sta­ ble complexes only with iron, and the stability of complexes with other necessary microele­ ments (Mn, Cu, Zn, Co) is significantly low­ er [55]. Therefore, in the modern practice of creating chelated microfertilizers, the EDDHA complex is used extremely rarely, although it is allowed by the European Union Directive EU 2003/2003 of October 13, 2003 for the produc­ tion of mineral fertilizers. 112 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY Fig. 8 – Comparison of Fe-chelate stabilities in soil solution [3]. 18 the complexes decreases as follows: EDDHA> DTPA> CDTA> EDTA> EDDS (Fig. 9) [3]. It should be noted that EDDHA has a high selectivity for Fe3+ in a wide pH range (from 4 to 9), but, unfortunately, this effective chelant forms stable complexes only with iron, and the stability of complexes with other necessary microelements (Mn, Cu, Zn, Co) is significantly lower [55]. Therefore, in the modern practice of creating chelated microfertilizers, the EDDHA complex is used extremely rarely, although it is allowed by the European Union Directive EU 2003/2003 of October 13, 2003 for the production of mineral fertilizers. . Fig. 8 – Comparison of Fe-chelate stabilities in soil solution [3]. There are various factors affecting the stability of metal chelates, which are primarily related to the nature of metals and the nature of the chelating agent (ligand). The influence of metal ions on the stability of chelates is manifested as follows: at the same degree of oxidation for metal ions of the same family (for example, 3d, alkaline earth elements), the stability of complexes increases with a decrease in the ionic radius. So for Ca(II) complexes lgKst. is higher than for the corresponding strontium complex. For the same metal, as the ion charge increases, the stability constant increases (for example, Fe3+ chelates are more stable than Fe2+ in most cases). And finally, stability depends on the electronegativity of the metal ion and increases as follows: (eV) Cu (1.9) > Fe (1.8) > Zn (1.6) > Mn (1.5) > Ca (1.0), which makes it possible to create a stronger covalent bond. The effect of stabilization of the complex due to the chelating agent depends on the structure of the ligand (stability increases with the formation of a larger number of metallocycles between the metal ion and the chelating agent), the affinity of cations to the donor atoms of the ligand (for example, for a zinc ion, when coordination bonds with donor atoms are formed, stability changes in the series S> N> O, while for Ca ions there is no significant difference between these three donors). The stability of the complexes is significantly affected by the steric effect. When the atoms are too close to each other, energy is wasted due to overlapping electron There are various factors affecting the sta­ bility of metal chelates, which are primarily re­ lated to the nature of metals and the nature of the chelating agent (ligand). The influence of metal ions on the stability of chelates is mani­ fested as follows: at the same degree of oxi­ dation for metal ions of the same family (for example, 3d, alkaline earth elements), the sta­ bility of complexes increases with a decrease in the ionic radius. So for Ca(II) complexes lgKst. is higher than for the corresponding strontium complex. For the same metal, as the ion charge increases, the stability constant increases (for example, Fe3+ chelates are more stable than Fe2+ in most cases). And finally, stability de­ pends on the electronegativity of the metal ion and increases as follows: (eV) Cu (1.9) > Fe (1.8) > Zn (1.6) > Mn (1.5) > Ca (1.0), which makes it possible to create a stronger covalent bond. The effect of stabilization of the complex due to the chelating agent depends on the structure of the ligand (stability increases with the formation of a larger number of metallo­ cycles between the metal ion and the chelat­ ing agent), the affinity of cations to the donor atoms of the ligand (for example, for a zinc ion, when coordination bonds with donor atoms are formed, stability changes in the series S> N> O, while for Ca ions there is no signi­ 113https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 ficant difference between these three donors). The stability of the complexes is significantly affected by the steric effect. When the atoms are too close to each other, energy is wasted due to overlapping electron clouds (Pauli – Born re­ pulsion), and this can affect the desired shape of the molecule (conformation) and reactivity. And different conformations in space have dif­ ferent levels of stability. Complexes that have a high entropy are more stable, since the most stable energy state is achieved in them. For example, for ethylene diamine tetraacetates of various metals, the entropy (ΔS25С) changes in the following order: +55 (Cu2+) = +55 (Zn2+)> +42 (Cu2+)> +41 (Mn2+)> +32 (Mg2+). Among complexones that contain carboxyl groups, DTPA is the most optimal, which al­ lows the use of complexones (especially iron) on carbonate soils in a wide pH range (even at pH above 8), where other complexones are ineffective. Although, it should be noted that currently microfertilizers based on EDTA are produced in the largest quantities, which is primarily due to its sufficient availability and relatively low cost. Currently, the vast majority of chelated mi­ crofertilizer preparations are based on com­ plexes of two complexones – ethylenediamine­ tetraacetic acid and hydroxyethylenediphos­ phonic acid. The leadership of these chelants is due, first of all, to their unique properties (the possibility of forming complexes with almost all metals of the Periodic System) in combi­ nation with a well-developed theoretical and experimental base and, of course, economic feasibility of use. Chelates are produced on the basis of EDTA, which can be used on soils with a pH of less than 8, and for each microelement, stable compounds can be formed only at cer­ tain pH values (for example, an iron complex with EDTA is effective in combating chlorosis only on moderately acidic soils; in an alkaline medium it is unstable. It should be noted seve­ ral characteristic features of complexes with EDTA: complexes with molybdenum are rela­ tively weak, they decompose in an alkaline en­ vironment; Ca and Mg chelates are soluble, but less stable compared to other trace elements; no complexes are formed with boron). In ad­ dition, chelates with EDTA are decomposed by soil microorganisms, which leads to the tran­ sition of trace elements to an insoluble form. These drugs exhibit antiviral activity. Of the complexones containing phosphonic groups, HEDP is the most promising. On its ba­ sis, all individual metal complexonates used in agriculture, as well as compositions of various compositions and ratios, can be obtained. In its structure, it is closest to natural compounds based on polyphosphates (during its decom­ position, chemical compounds are formed that are easily absorbed by plants). Chelates based on it can be used on soils with a pH of 4.5–11. A distinctive feature of this chelating agent is that, unlike EDTA, it can form stable complex­ es with Mo and B. However, it is a very weak chelating agent for iron, copper, and zinc. In the nutrient solution or root zone, these ions are easily replaced by calcium and their effec­ tiveness is significantly reduced. HEDP is re­ sistant to the action of soil microorganisms. The conditions of solubility of HEDP complex­ es, which are strictly differentiated depending on the complexing metal, make it possible to obtain microfertilizers of prolonged action. The specificity of the interaction of OEDP with calcium ions allows changing the physi­ cochemical and granulometric properties of various mineral fertilizers. It should be not­ ed that the use of HEDP-based chelates in 114 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY working solutions on very hard natural waters is unacceptable, however, acidification elimi­ nates this drawback. In addition, HEDP pre­ vents the formation of poorly soluble salts in nozzles, pipelines of nutrient systems and is a growth regulator. The formation of stable complexes of metals with HEDP can be explained by the formation of chelate structures due to the bidentate coor­ dination of the ligand by two oxygen atoms of phosphonic groups to the cation. At the same time, stable eight-membered cycles are formed, which can be strengthened by intramolecular bonds with the participation of water mole­ cules, formed in the case of the interaction of a metal cation with the oxygen atoms of two phosphate groups at the same time, which can be strengthened by intramolecular bonds with the participation of water molecules: Нydroxyethylidenediphosphonic acid is close in its structure to natural compounds based on polyphosphates (its decomposition produces chemical compounds easily digested by plants). Other complexones are also used as chelat­ ing agents, for example, ethylenediamine (2-hydroxy-4-methylphenyl)acetic acid. Che­ lates based on it can be used in pH ranges from 3.5 to 11.0. However, the cost of this highly ef­ fective agent is quite significant. The issues of the use of 3-d metal complexes based on eth­ ylenediaminedisuccinic acid are covered quite widely in the literature. These complexes are very stable (lgKst.~13–18) in a wide pH range (3–10) and are biologically active, non-toxic and environmentally friendly compounds [56, 57]. The type of chelating agent strongly affects the efficiency of the fertilizer and the degree of assimilation of trace elements by the plant: chelates based on lignins are absorbed 4 times better, those based on citrates 6 times better, and those based on classical aminopolycar­ boxylates and/or polyphosphonates (EDTA, HEDP, DTPA) – in 8–10 times better than tra­ ditional inorganic fertilizers [58]. In chelated microfertilizers based on traditional comple­ xones such as EDTA, DTPA, NTA, HEDP, the active component is only the ion of a biologi­ cally active trace element, and the organic part of the compounds performs only a transport function – diffuse delivery of trace elements to plants. In complexes based on EDDS, the chelant not only delivers the trace element, but also has a biological activity itself. Upon en­ tering to a living organism, the organic part of ethylene diamine disuccinates under the influ­ ence of sunlight or UV radiation breaks down into essential amino acids (arginine, leucine, isoleucine, valine, histidine, asparagine, ala­ nine), which are present in the living organism as components of the metabolic chain (Fig. 9, table 4) [59–61]. Fig. 9 – Chromatogram of photolysis products of FeІІІEDDS model solutions (C=1·10-3 mol/l) after irradiation λ=345 nm [60, 61]. 19 clouds (Pauli – Born repulsion), and this can affect the desired shape of the molecule (conformation) and reactivity. And different conformations in space have different levels of stability. Complexes that have a high entropy are more stable, since the most stable energy state is achieved in them. For example, for ethylene diamine tetraacetates of various metals, the entropy (ΔS25С) changes in the following order: +55 (Cu2+) = +55 (Zn2+)> +42 (Cu2+)> +41 (Mn2+)> +32 (Mg2+). Among complexones that contain carboxyl groups, DTPA is the most optimal, which allows the use of complexones (especially iron) on carbonate soils in a wide pH range (even at pH above 8), where other complexones are ineffective. Although, it should be noted that currently microfertilizers based on EDTA are produced in the largest quantities, which is primarily due to its sufficient availability and relatively low cost. Currently, the vast majority of chelated microfertilizer preparations are based on complexes of two complexones – ethylenediaminetetraacetic acid and hydroxyethylenediphosphonic acid. The leadership of these chelants is due, first of all, to their unique properties (the possibility of forming complexes with almost all metals of the Periodic System) in combination with a well-developed theoretical and experimental base and, of course, economic feasibility of use. Chelates are produced on the basis of EDTA, which can be used on soils with a pH of less than 8, and for each microelement, stable compounds can be formed only at certain pH values (for example, an iron complex with EDTA is effective in combating chlorosis only on moderately acidic soils; in an alkaline medium it is unstable. It should be noted several characteristic features of complexes with EDTA: complexes with molybdenum are relatively weak, they decompose in an alkaline environment; Ca and Mg chelates are soluble, but less stable compared to other trace elements; no complexes are formed with boron). In addition, chelates with EDTA are decomposed by soil microorganisms, which leads to the transition of trace elements to an insoluble form. These drugs exhibit antiviral activity. Of the complexones containing phosphonic groups, HEDP is the most promising. On its basis, all individual metal complexonates used in agriculture, as well as compositions of various compositions and ratios, can be obtained. In its structure, it is closest to natural compounds based on polyphosphates (during its decomposition, chemical compounds are formed that are easily absorbed by plants). Chelates based on it can be used on soils with a pH of 4.5–11. A distinctive feature of this chelating agent is that, unlike EDTA, it can form stable complexes with Mo and B. However, it is a very weak chelating agent for iron, copper, and zinc. In the nutrient solution or root zone, these ions are easily replaced by calcium and their effectiveness is significantly reduced. HEDP is resistant to the action of soil microorganisms. The conditions of solubility of HEDP complexes, which are strictly differentiated depending on the complexing metal, make it possible to obtain microfertilizers of prolonged action. The specificity of the interaction of OEDP with calcium ions allows changing the physicochemical and granulometric properties of various mineral fertilizers. It should be noted that the use of HEDP-based chelates in working solutions on very hard natural waters is unacceptable, however, acidification eliminates this drawback. In addition, HEDP prevents the formation of poorly soluble salts in nozzles, pipelines of nutrient systems and is a growth regulator. The formation of stable complexes of metals with HEDP can be explained by the formation of chelate structures due to the bidentate coordination of the ligand by two oxygen atoms of phosphonic groups to the cation. At the same time, stable eight-membered cycles are formed, which can be strengthened by intramolecular bonds with the participation of water molecules, formed in the case of the interaction of a metal cation with the oxygen atoms of two phosphate groups at the same time, which can be strengthened by intramolecular bonds with the participation of water molecules: 20 Нydroxyethylidenediphosphonic acid is close in its structure to natural compounds based on polyphosphates (its decomposition produces chemical compounds easily digested by plants). Other complexones are also used as chelating agents, for example, ethylenediamine (2- hydroxy-4-methylphenyl)acetic acid. Chelates based on it can be used in pH ranges from 3.5 to 11.0. However, the cost of this highly effective agent is quite significant. The issues of the use of 3-d metal complexes based on ethylenediaminedisuccinic acid are covered quite widely in the literature. These complexes are very stable (lgKst.~13–18) in a wide pH range (3–10) and are biologically active, non-toxic and environmentally friendly compounds [56, 57]. The type of chelating agent strongly affects the efficiency of the fertilizer and the degree of assimilation of trace elements by the plant: chelates based on lignins are absorbed 4 times better, those based on citrates 6 times better, and those based on classical aminopolycarboxylates and/or polyphosphonates (EDTA, HEDP, DTPA) – in 8–10 times better than traditional inorganic fertilizers [58]. In chelated microfertilizers based on traditional complexones such as EDTA, DTPA, NTA, HEDP, the active component is only the ion of a biologically active trace element, and the organic part of the compounds performs only a transport function – diffuse delivery of trace elements to plants. In complexes based on EDDS, the chelant not only delivers the trace element, but also has a biological activity itself. Upon entering to a living organism, the organic part of ethylene diamine disuccinates under the influence of sunlight or UV radiation breaks down into essential amino acids (arginine, leucine, isoleucine, valine, histidine, asparagine, alanine), which are present in the living organism as components of the metabolic chain (Fig. 9, table 4) [59–61]. Fig. 9 – Chromatogram of photolysis products of FeІІІEDDS model solutions (C=1·10-3 mol/l) after irradiation λ=345 nm [60, 61]. Table 4. Products of the photochemical decomposition of Fe(ІІІ) and Mn(ІІ) complexonates with ethylenediaminedisuccinic acid. FеЕDDS МnЕDDS NН3 – 68% NН3 – 89% СО2 – 82% СO2 – 68% – Alanin (Ala) – 0,35% Arginine (Аrg) – 6,3% Arginine (Arg) – 3,89% Asparagine (Asp) – 1,9% Asparagine (Asp) – 1,8% Valine (Val) – 0,72% - Histidine (His) –13,9% Histidine (His) – 9,8% Isoleucine (Ile) – 0,76% Isoleucine (Ile) – 0,87% Leucine (Leu) –1,4% Leucine (Leu) – 2,7% Glutamine (Gln) – 1,34% – Phenylalanine (Phe) - 11,3% – 115https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Table 4. Products of the photochemical decomposition of Fe(ІІІ) and Mn(ІІ) complexonates with ethylenediaminedisuccinic acid. FеЕDDS МnЕDDS NН3 – 68% NН3 – 89% СО2 – 82% СO2 – 68% – Alanin (Ala) – 0,35% Arginine (Аrg) – 6,3% Arginine (Arg) – 3,89% Asparagine (Asp) – 1,9% Asparagine (Asp) – 1,8% Valine (Val) – 0,72% - Histidine (His) –13,9% Histidine (His) – 9,8% Isoleucine (Ile) – 0,76% Isoleucine (Ile) – 0,87% Leucine (Leu) –1,4% Leucine (Leu) – 2,7% Glutamine (Gln) – 1,34% – Phenylalanine (Phe) - 11,3% – Depending on the 3d-metal, a different set of essential amino acids is formed when the complexes decompose, which is obviously as­ sociated with the different nature of the me­ tal and the stability of the complexes. But the main decomposition products are ammonia and CO2. The given data show that compounds, the cation of which can change the valence state, undergo photochemical decomposition in solution. The photodecomposition of com­ plexes is accompanied, first of all, by decarbox­ ylation processes with release of free CO2, as well as ammonia. The depth of decomposition increases with increasing pH and the intensity of irradiation. Since the final products of the photolysis of complexonates are natural ami­ no acids containing residues characteristic of the EDDS molecule, it can be assumed that the photodecomposition is accompanied not only by the breaking of the bond in the original EDDS molecule, but also by the recombination of the emerging intermediate products. The question of the important role of pho­ tochemical redox reactions of iron-containing chelates (the transition of Fe(III) to Fe(II)) is discussed in [62]. For the implementation of metabolic processes in plants, a divalent form of iron is needed. The key value of Fe(II) is de­ termined, on the one hand, by the better solu­ bility of its mineral salts compared to Fe(III), and, on the other hand, by the lower stability of Fe(II)-chelates, which facilitates the release of iron from transport forms and its further in­ corporation into metabolism. The photoreduc­ tion of Fe(III) to Fe(II) occurs under the action of optical radiation with wavelengths less than 420 nm. Optical radiation with a wavelength distribution in the range of 350–700 nm is able to penetrate the green leaf and cause photore­ duction of Fe (III) in the nutrient solution. This process occurs both with direct irradiation of 116 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY solutions and with their illumination through leaves affected by chlorosis. With the exclusion of the ultraviolet part from the composition of optical irradiation, the photoreduction of Fe (III) is suppressed. The stimulating effect of UV radiation on the reduction of Fe(III) and the synthesis of chlorophyll in leaves was found in experiments with soybean plants, in which, under the influence of UV rays, physiological effects were enhanced and accompanied by an increase in the amount of chlorophyll and ca­ rotenoids. The mechanism of photolysis of carboxyl- containing chelates of iron and other trace ele­ ments (Mn, Co) consists in the elimination of the CO2 molecule and the consequent reduc­ tion of the chelate cycle. During photolysis, in­ termediate products with metal-carbon bonds are formed. These products are thermally un­ stable and form metal ions as well as ligand ra­ dicals. For example, the photodecomposition of Fe-chelates of citric or tartaric acids is accom­ panied by the formation of numerous inter­ mediate compounds, and the end products of decomposition are acetone and carbon dioxide. During the photodecomposition of EDTA, the following products have been identified: car­ bon dioxide, formaldehyde, ethylenediamine­ triacetate, ethylenediaminediacetate ions. In [61], based on the results of mass spec­ trometry of metal complexes with ethylene­ diaminediansuccinic acid, it was established that the decomposition of the compounds is accompanied by the breaking of the C–N bond and intramolecular rearrangement along the labile bonds of the ethylene bridge with the formation of certain amino acid radicals or amino acids themselves. (Table 5). Table 5. Ratio of the mass to the charge of fragments and their interpretation in the mass spectra of Fe (III) and Mn(II) complexes with EDDS. m/z Fragment Interpretation EDDS FeEDDS MnEDDS 55 64 – -NH2-CH2-CH2-NH2- Ethylenediamine / Ethylenediamine radical 69 69 69 -HC-NH-(CH2)2-NH- Fragment EDDS – 75 75 -NH-CH-COOH Glycine 86 84 84 -NH-CH-(СООН)-CH2- α- Alanin 96 98 96 -NH-CH(СО-)CH2-СО- Asparagine fragment 101 – – -CH2-CH2-СН(NH)COOH Aminobutyric acid 112 112 112 -CH(COO-)CH-COO- Succinic acid radical – 121 – HOOC-CH2-CH2-COOH Succinic acid – 130 – -NH-CH(СООН)-CH2-COOH β-Asparagine – 149 – HOOC-(CH2)2-CH(COOH)NH2 Glutamic acid 158 – – HOOC-CH2-СН(СООН)NH-(CH2)2- – 296 296 – EDDS 117https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Compared to the mass spectra of pure EDDS, a larger set of decay products is observed in the complexes, because the attachment of a metal to the complex one weakens the carbon-nitro­ gen bond due to the coordination of the cation of amino groups and increases the mobility of the asparagine fragment of EDDS. The decom­ position products of ethylenediaminesuccinic acid and its complexes are mainly natural com­ pounds, which determines the environmental safety and biological activity of both EDDS it­ self and its complexes with microelements. The study of the stimulating effect of the FeEDDS complex compared to the effect of the natural growth stimulator heteroauxin (HA) on the growth processes of corn showed that under the influence of the complex, the length of the leaf and root increases by ~ 45%, while heteroauxin increases these indicators by ~ 38% [61]. In this case, the stimulation by FeEDDS by more significant than that by NA precisely on the leaves, which are the surface part of the plant. Presumably, in this case, the photodestruction of the complexonate under the action of natural light is more pronounced. Under the influence of the FeEDDS com­ plex, the content and heterogeneity of free amino acids (alanine, asparagine, glutamine, glycine, threonine, serine, tyrosine, etc.) in plants increases (Table 6). In general, the total amount of amino acids under the action of the complexing agent increases sharply, in addi­ tion, there is an increase in the heterogeneity of free amino acids. Also, a distinction of their qualitative com­ position under the conditions of stimulation from that under the conditions of inhibition is the absence of an increase in the «non-damag­ ing2 osmolyte of the cell, while its significant accumulation is observed under saline condi­ tions. This is due to the fact that this is how the plant reacts to stressful conditions for it, when growth processes are inhibited. In addition, this is explained by the different compartmen­ talization of the enzymes for the synthesis and breakdown of proline located in mitochondria. Under saline conditions, the proportion of pro­ line in mitochondrial membranes decreases and, therefore, its decomposition cannot occur. Table 6. The content of amino acids in the leaves of corn seedlings. Amino acid Control Experiment Alanine 12,20 15,8 Methionine 3,12 0,97 Valin 4,63 1,45 Leucine 6,04 4,53 Isoleucine 5,26 5,34 Proline 8,78 7,35 Threonine – 3,27 Serin – 2,44 γ-Aminobutyric acid 7,39 7,68 Arginine 2,39 3,33 Glutamine 4,06 5,55 Asparagine 30,88 33,77 Glycine 2,49 24,01 Lysine 2,45 2,26 Tyrosine – 1,74 Phenylalanine – 5,43 Histidine – 1,66 Amount, % 0,19 0,39 Based on the results obtained, taking into account the data of [63, 64], an assumption was made about the mechanism of action of FeEDDS complexonate in plants. 118 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY The tricarboxylic acid cycle (TCAC) is a key step in the respiration of all cells that use oxygen, the intersection point of many meta­ bolic pathways in the body, an intermediate step between glycolysis and the electron trans­ port chain. In addition to a significant ener­ gy role, the cycle also performs a significant plastic function, that is, it is an important source of precursor molecules, from which, in the course of other biochemical transfor­ mations, such important compounds for cell life as amino acids, carbohydrates, fatty acids, etc. are synthesized. The tricarboxylic acid cycle includes 8 main stages, including the oxidation of isocitrate to α-ketoglutarate, the oxidation of α-ketoglutarate to succinyl-CoA, the conversion of succinyl-CoA to succinate. It was shown in [63] that the amino acids his­ tidine, proline, arginine, glutamine, and glu­ tamate can be converted into α-ketoglutarate and restore its concentration; isoleucine, va­ line, methionine, tryptophan - into succinyl- CoA, aspartate, phenylalanine and tyrosine into fumarate; aspartate and aspragine to ox­ aloacetate. The amino acids alanine, serine, threonine, cysteine and glycine can be con­ verted into pyruvate, which is necessary for the tricarboxylic acid cycle (Fig. 10). Fig. 10 – Scheme of the inclusion of amino acids in the tricarboxylic acid cycle [63]. 23 enzymes for the synthesis and breakdown of proline located in mitochondria. Under saline conditions, the proportion of proline in mitochondrial membranes decreases and, therefore, its decomposition cannot occur. Based on the results obtained, taking into account the data of [63, 64], an assumption was made about the mechanism of action of FeEDDS complexonate in plants. The tricarboxylic acid cycle (TCAC) is a key step in the respiration of all cells that use oxygen, the intersection point of many metabolic pathways in the body, an intermediate step between glycolysis and the electron transport chain. In addition to a significant energy role, the cycle also performs a significant plastic function, that is, it is an important source of precursor molecules, from which, in the course of other biochemical transformations, such important compounds for cell life as amino acids, carbohydrates, fatty acids, etc. are synthesized. The tricarboxylic acid cycle includes 8 main stages, including the oxidation of isocitrate to α-ketoglutarate, the oxidation of α-ketoglutarate to succinyl-CoA, the conversion of succinyl-CoA to succinate. It was shown in [63] that the amino acids histidine, proline, arginine, glutamine, and glutamate can be converted into α-ketoglutarate and restore its concentration; isoleucine, valine, methionine, tryptophan - into succinyl-CoA, aspartate, phenylalanine and tyrosine into fumarate; aspartate and aspragine to oxaloacetate. The amino acids alanine, serine, threonine, cysteine and glycine can be converted into pyruvate, which is necessary for the tricarboxylic acid cycle (Fig. 10). Fig. 10 – Scheme of the inclusion of amino acids in the tricarboxylic acid cycle [63]. In plants, during the glyoxylate cycle, acetyl-CoA is converted into succinate, which is further involved in biosynthetic processes [64]. The increase in the pool of free amino acids in plants under the influence of FeEDDS occurs due to a significant increase in the content of glutamine – one of the main transport forms of nitrogen. As is known that glutamine in the plant is formed from -ketoglutarate (Fig. 11). The FeEDDS complex includes two succinate fragments. Therefore, it can be assumed that these 119https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 In plants, during the glyoxylate cycle, acetyl- CoA is converted into succinate, which is fur­ ther involved in biosynthetic processes [64]. The increase in the pool of free amino acids in plants under the influence of FeEDDS oc­ curs due to a significant increase in the content of glutamine – one of the main transport forms of nitrogen. As is known that glutamine in the plant is formed from α-ketoglutarate (Fig. 11). The FeEDDS complex includes two succi­ nate fragments. Therefore, it can be assumed that these succinate residues are included in the tricarboxylic acid cycle, going the path to α-ketoglutarate and, thus, accelerate the main substrate- and energy-providing process of the TCAC. 24 succinate residues are included in the tricarboxylic acid cycle, going the path to -ketoglutarate and, thus, accelerate the main substrate- and energy-providing process of the TCAC. Fig. 11 – Formation of glutamine in a plant cell. It is also possible that metal complexes with EDDS somehow activate the path of tryptophan synthesis or are directly included in this path, and tryptophan is a precursor of auxin – a plant growth hormone. APPLICATION OF COMPLEXONATES OF MICROELEMENTS IN PLANT BREEDING. The use of chelate microelements based on complexonates is very wide, since they allow providing plants with the necessary microelements by converting ME into a mobile biologically active form not only in plants, but also in the soil. Metal complexonates used as microfertilizers are the most effective form of micronutrients and a means of regulating the production process of agricultural crops, both during seed treatment before sowing and during root and foliar top dressing [65]. With their help, you can easily correct nutritional deficiencies that occur as the plant develops (Fig. 12). Especially valuable is the use of chelates at an early stage of development, when the root system is not yet well formed. In the flowering stage, the use of foliar dressings with chelates increases the number of ovaries, and fruit processing increases their sugar content. Fig.12 – The need of plants for microelements in various phases of growth. Chelates are compatible with insecticides and pesticides and when used together reduce plant stress due to the application of pesticides. Мicroelements in chelated form, enhance plant immunity and serve as a prophylactic against fungal and viral diseases. Fig. 11 – Formation of glutamine in a plant cell. 24 succinate residues are included in the tricarboxylic acid cycle, going the path to -ketoglutarate and, thus, accelerate the main substrate- and energy-providing process of the TCAC. Fig. 11 – Formation of glutamine in a plant cell. It is also possible that metal complexes with EDDS somehow activate the path of tryptophan synthesis or are directly included in this path, and tryptophan is a precursor of auxin – a plant growth hormone. APPLICATION OF COMPLEXONATES OF MICROELEMENTS IN PLANT BREEDING. The use of chelate microelements based on complexonates is very wide, since they allow providing plants with the necessary microelements by converting ME into a mobile biologically active form not only in plants, but also in the soil. Metal complexonates used as microfertilizers are the most effective form of micronutrients and a means of regulating the production process of agricultural crops, both during seed treatment before sowing and during root and foliar top dressing [65]. With their help, you can easily correct nutritional deficiencies that occur as the plant develops (Fig. 12). Especially valuable is the use of chelates at an early stage of development, when the root system is not yet well formed. In the flowering stage, the use of foliar dressings with chelates increases the number of ovaries, and fruit processing increases their sugar content. Fig.12 – The need of plants for microelements in various phases of growth. Chelates are compatible with insecticides and pesticides and when used together reduce plant stress due to the application of pesticides. Мicroelements in chelated form, enhance plant immunity and serve as a prophylactic against fungal and viral diseases. Fig.12 – The need of plants for microelements in various phases of growth. 120 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY Fig. 13 – Mechanism of metal (Fe) release from chelating agent [3]. 25 In complexonates organic acid significantly increases the solubility of the microelement ion in solution; transports the microelement ion into the plant organism; protects the microelement ion from transformations of physical and chemical nature; promotes the rapid involvement of microelement ion in biochemical processes in the plant organism (Fig.13) [3]. Fig. 13 – Mechanism of metal (Fe) release from chelating agent [3]. The main role of chelates is to keep the metal cations in solution so they can diffuse through the soil to the roots. This is done through the formation of a chelate "ring" around the metal cation, which protects the metal from interaction with other inorganic compounds. Upon reaching the plant root, the metal cation either splits out from the chelate and diffuses into the root membrane, or the entire metal chelate complex is absorbed into the root and then decomposes, releasing the metal. Both cases result in the extraction of the metal up the root, and the chelate is returned to the soil solution for binding other metals. Applying to the soil and spraying with solutions of complexonates of microelements have a positive effect on the yield of many crops [66–77]. For example, treatment with manganese, iron, copper, etc. Complexonates on based EDTA and DTPA, of the seeds of cereal, industrial, grain crops (buckwheat, oats, barley, rye, flax) lead to a change in the terms of plant vegetation, accelerates the germination of these crops, and increases their yield. In [77] the effect of chelate compounds of zinc, copper, manganese and iron with HEDP on the yield of spring rapeseed, white lupine and oats was studied. For comparison, traditional forms of trace elements were used – vitriol of the corresponding metals. It was found that the chelated forms of microelements had an advantage over their salt counterparts, providing a biomass yield of rapeseed pods higher than the best of the options using sulfate for zinc by 56%, for copper – 38%, for manganese – 42%, as well as an increase in oat grain by 18%. % when using iron. Also, the individual characteristics of plants in relation to the studied microelements were revealed. Thus, the treatment of spring rapeseed with chelates containing zinc and copper contributed to the greater development of generative organs. In [73], a heterometallic complex of magnesium and germaniumIV based on HEDP – [Mg(H2O)6]3[Ge6(μ-OH)6(μ-HEDP)6]∙20Н2О – was used for the pre-sowing treatment of winter wheat seeds. It has been proven that the compound increases the field germination of wheat by 75%. In addition, intensive growth of ground mass (17 cm) and primary root system (7.5 cm) was observed in the plants. These indicators are significantly higher compared to the control and standard – complex fertilizer Novalon. During clonal micropropagation of the gooseberry cultivar at the stage of rhizogenesis, the efficiency of modification of media with mineral salts according to Quoirin-Lepoivre (QL) was shown by replacing iron, which is standardly used in the form of FeSO4·7H2O together with It is also possible that metal complexes with EDDS somehow activate the path of trypto­ phan synthesis or are directly included in this path, and tryptophan is a precursor of auxin – a plant growth hormone. APPLICATION OF COMPLEXONATES OF MICROELEMENTS IN PLANT BREED- ING. The use of chelate microelements based on complexonates is very wide, since they al­ low providing plants with the necessary mic­ roelements by converting ME into a mobile biologically active form not only in plants, but also in the soil. Metal complexonates used as microfertilizers are the most effective form of micronutrients and a means of regulating the production process of agricultural crops, both during seed treatment before sowing and during root and foliar top dressing [65]. With their help, you can easily correct nutritional deficiencies that occur as the plant develops (Fig. 12). Especially valuable is the use of che­ lates at an early stage of development, when the root system is not yet well formed. In the flowering stage, the use of foliar dressings with chelates increases the number of ovaries, and fruit processing increases their sugar content. Chelates are compatible with insecticides and pesticides and when used together reduce plant stress due to the application of pesticides. Мicroelements in chelated form, enhance plant immunity and serve as a prophylactic against fungal and viral diseases. In complexonates organic acid significant­ ly increases the solubility of the microelement ion in solution; transports the microelement ion into the plant organism; protects the micro­ element ion from transformations of physical and chemical nature; promotes the rapid in­ volvement of microelement ion in biochemical processes in the plant organism (Fig.13) [3]. 121https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 The main role of chelates is to keep the metal cations in solution so they can diffuse through the soil to the roots. This is done through the formation of a chelate "ring" around the metal cation, which protects the metal from interac­ tion with other inorganic compounds. Upon reaching the plant root, the metal cation either splits out from the chelate and diffuses into the root membrane, or the entire metal chelate complex is absorbed into the root and then de­ composes, releasing the metal. Both cases re­ sult in the extraction of the metal up the root, and the chelate is returned to the soil solution for binding other metals. Applying to the soil and spraying with solu­ tions of complexonates of microelements have a positive effect on the yield of many crops [66–77]. For example, treatment with man­ ganese, iron, copper, etc. Complexonates on based EDTA and DTPA, of the seeds of cereal, industrial, grain crops (buckwheat, oats, bar­ ley, rye, flax) lead to a change in the terms of plant vegetation, accelerates the germination of these crops, and increases their yield. In [77] the effect of chelate compounds of zinc, copper, manganese and iron with HEDP on the yield of spring rapeseed, white lupine and oats was studied. For comparison, traditional forms of trace elements were used – vitriol of the corre­ sponding metals. It was found that the chelated forms of microelements had an advantage over their salt counterparts, providing a biomass yield of rapeseed pods higher than the best of the options using sulfate for zinc by 56%, for copper – 38%, for manganese – 42%, as well as an increase in oat grain by 18%. % when us­ ing iron. Also, the individual characteristics of plants in relation to the studied microelements were revealed. Thus, the treatment of spring rapeseed with chelates containing zinc and copper contributed to the greater development of generative organs. In [73], a heterometallic complex of magnesium and germaniumIV based on HEDP – [Mg(H2O)6]3[Ge6(μ-OH)6 (μ-HEDP)6]∙20Н2О – was used for the pre-sow­ ing treatment of winter wheat seeds. It has been proven that the compound increases the field germination of wheat by 75%. In addition, intensive growth of ground mass (17 cm) and primary root system (7.5 cm) was observed in the plants. These indicators are significantly higher compared to the control and standard – complex fertilizer Novalon. During clonal micropropagation of the gooseberry cultivar at the stage of rhizogene­ sis, the efficiency of modification of media with mineral salts according to Quoirin-Lepoivre (QL) was shown by replacing iron, which is standardly used in the form of FeSO4·7H2O together with Na2EDTA, with chelated forms with carboxyl-containing ligands Fe(III)-ED­ TA and Fe(III)-DTPA and the organophos­ phate complexone Fe(II)-HEDP. On the 45th and 60th days of subculturing, the distribu­ tion in descending order of the impact of che­ late iron compounds on the rooting rate of the studied gooseberry plants was as follows: Fe(III)-EDTA>Fe(III)-DTPA> Fe(II) -HEDP> Fe(III)-EDDHA>Fe(III)-HEDP. On the 60th day of subculturing in the best variants of the experiment, the rooting rate of gooseberry mi­ crocuttings of cultivar Pink-2 was 86.7-100% compared to 60% in the control variant [74]. The effect of organic (Fe-EDTA and Fe-ED­ DHA) and inorganic (FeCl3) iron substanc­ es on the rooting of the rootstock GF-677 (Prunus amygdalus×Prunus persica – hybrid of peach and almond) in vitro was studied. Full rooting (100 %) was observed in ex­ plants nourished with Fe-EDDHA, while less 122 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY rooting was found in the absence of iron or in the presence of FeCl3. On the contrary, no root formation was observed in explants nourished with Fe-EDTA, which showed extremely lower chlorophyll and high iron contents at the end of the experiment [71]. Complexes of 3d-metals with EDDS are en­ vironmentally safe biostimulants and positive­ ly affect the yield of plants (apple trees, straw­ berries, legumes, cabbage, buckwheat, alfalfa, etc.) [72, 74–77]. Fe[S,S']-EDDS was evaluated as an iron-containing fertilizer in growing ca­ lendula [78]. It has been shown that FeEDDS complexes are a suitable source of Fe for the production of marigolds and, most likely, oth­ er horticultural crops. Iron sources (FeEDDS, FeEDTA, FeDTPA, FeEDDHA, and FeSO4) did not affect marigold leaf count, plant height, dry weight, or leaf greenness, and there was no evi­ dence of bronze spotting or micronutrient toxi- city syndrome. At the same time, all the main indicators of the development of calendula leaves when using chelate complexes and fer­ rous sulfate did not differ much and were suf­ ficient for normal growth. However, obtaining concentrated initial solutions of fertilizers with non-chelate microfertilizers turned out to be practically impossible due to the low solubility of the iron salt. Therefore, APCA complexones (chelates) are necessary to maintain the solu­ bility of this metal. And the best fertilizer to use are FeEDDS/EDDS chelates. In [79], it was established that no nega­ tive consequences are observed when using FeEDDS on peat soils to increase the yield of fruit and vegetable crops. The work [80] com­ pared the mobility, leaching and availability of ionc of zinc when using its various complexo­ nates (ZnHEDTA, ZnEDDHSA, ZnEDTA, Zn(S,S)EDDS) on haricot bean. It was estab­ lished that the maximum concentration of zinc in soil leachate was 65 mg/l for Zn(S,S)EDDS when 10 mg of Zn was applied per 1 kg of soil. At the same time, the pH of the calcareous soil increased significantly over the course of the experiment. The effect of presowing treatment of spinach seeds with compounds containing complexo­ nes (EDDS, IDS), as well as their complexo­ nates with magnesium and zinc, on the content of chlorophylls and carotenoids in plant leaves was studied. The effect of complexons was studied in combination with the exposure of seeds to a weak constant magnetic field. An in­ crease in the content of pigments, participants in the process of photosynthesis, was record­ ed in spinach plants [81]. In the presence of 50 µmol/L Cu, the addition of edds increased the growth of shoots and roots and decreased the relative loss of electrolyte from the root cells of chrysanthemum (Chrysanthemum coronari- um L.), which led to an increase in the accumu­ lation of copper in plant shoots [82]. The results of studies of the effect of EDDS and its complexes with boron showed a signifi­ cant efficiency of using borate complexes in comparison with the traditional boron micro­ fertilizer H3BO3 as stimulators of soil biologi­ cal activity and photosynthetic processes in order to obtain an optimal yield of table beet root crops [83]. It has been proven that EDDI­ AC has a pronounced antimicrobial effect, and B-EDDS stimulates the microflora. Treatment with B-EDDS solution caused an increase in leaf weight by 19% and in root crops by 37%. The effect of boron compounds on the germi­ nation, biomass, and pigment composition of seedlings of flax, wheat, and Kalanchoe pin­ nate, as well as on the nutrient content of Jeru­ salem artichoke tubers, was studied [84]. Seed 123https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 germination in a solution of boroethylenedi­ amine disuccinate significantly increased the level of chlorophyll content of flax seedlings. Treatment with boric acid and free ligand EDDS also caused some increase in biological­ ly active substances. Apparently, not only bo­ ron, but also EDDS is included in the metabol­ ic processes of the plant as an additional source of organic carbon and amine nitrogen. The ob­ tained data showed that the EDDS borate com­ plex turned out to be a more effective fertilizer for the plant than boric acid or EDDS alone. The use of B-EDDS significantly increased the level of chlorophyll in the leaves and seedlings of wheat, of sugars and pectin in the leaves of Kalanchoe, inulin and fructose in Jerusalem artichoke tubers. Some addition of biologically active substances was also caused by treatment with boric acid and a free ligand. Apparently, not only boron, but also complexone is includ­ ed in the metabolic processes of the plant as an additional source of organic carbon. At the same time, as part of the complex, both com­ ponents of the test preparation are more acces­ sible to plants than each separately. Employees of the V.I. Vernadsky Institute of General and Inorganic Chemistry of National Academy of Sciences of Ukraine have worked, for a number of years to create new chelate forms of microfertilizers based on complex­ es of Mn(II), Fe(III), Co(II), Cu(II), Zn(II) with EDDS [61, 72, 75, 76 , 85–88]. The effect of complexonates on increasing the yield of fodder (rapeseed, clover, sweet clover, lupine, etc.), technical (alfalfa, buckwheat, corn), veg­ etable (beets, tomatoes, cabbage) crops, grapes, flowers was studied in a field experiment in different regions of Ukraine. Plants were treated during the period of budding by fo­ liar feeding or pre-sowing treatment of grains with aqueous solutions of preparations with a metal concentration of 0.05 wt.%. It has been established that under the action of complexo­ nates, the yield of plants increases (15–50%), the quality of the fodder mass and grain im­ proves (the content of sugar, fiber, fats and pro­ teins increases). In grape berries, sugar content increases by 10-12%, and in leaves – the con­ tent of chlorophylls and carotenoids increas­ es by 59% and 30%, respectively). The use of preparations on flowers significantly increases the number of productive stems: by 22% for carnations and by 42% for roses. In addition, for roses, an improvement in the elitism of the variety was noted – an increase and compac­ tion of buds. In addition to growth-stimulating copper complexes, they exhibit a pronounced fungicidal effect. The addition of a second biologically active ligand (citric, tartaric acids, thiourea) or metal to ethylenediamine disuccinates made it possi­ ble to increase the biological activity of the com­ plexes. For example, when grapes were treated with the heterometallic complex, FeCuEDDS, increased by 7% compared to FeEDDS with monometallic iron complexonate. In that case, the absolute content of chlorophylls and caro­ tenoids increased by 79% and 37% for the mo­ nometal complex and by 93% and 48% for the heterometallic complex [87]. On the crops of oats and various herbs (natural meadow grasses), the heterometallic complex CuCoEDDS was tested, which in­ creased the yield of plants by 23% and 13% respectively. Also, in plants, the amount of microelements increases greatly: Cu2+ and Co2+ (by 38%), crude fat, protein and cellulose (~ 80%) [61]. When lupine and rapeseed plants are treated with solutions of the MnZnEDDS complex, the yield of both crops increases by 124 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY 20% compared to MnEDDS and ZnEDDS. The content of protein, crude fat and gluten, sugars increases in plant grains (Table 7). At the same time, the efficiency of microelements contained in complexonates is much higher (especially in the case of MnZnEDDS) than when using aqueous solutions of inorganic salts [88, 89]. Mixed-ligand ethylenediaminedisuccinate complexes of iron and copper with hydroxy acids and thiourea (THIO) also increase the yield and quality of grapes, barley, tomatoes, and peas compared to their monoligand coun­ terparts. At the same time, under the action of CuEDDSTHIO, the number of pea plants af­ fected by root rot decreased by 6.2% [61]. Table 7. Influence of foliar application of the complexes MnEDDS, ZnEDDS, MnEDDS on the accumulation of some metabolites in rape straw and grain. Оption Crude protein, g/kg Crude fat, g/kg Raw gluten, g/kg Sugar, g/kg straw grain straw grain straw grain straw grain control 18,4 169 6,3 353 25,4 109 16,3 35,4 MnSO4 17,7 179 6,2 374 24,7 95 15,5 37,6 ZnSO4 20,4 182 6,6 330 23,8 121 17,2 33,7 MnEDDS 20,0 178 6,6 376 25,7 122 16,9 37,7 ZnEDDS 21,7 175 6,8 342 27,9 128 17,2 38,8 MnZnEDDS 22,6 190 6,8 390 28,6 129 18,0 40,2 It is promising to use 3d-metal complexo­ nates for the treatment of carbonate chlorosis in grapes and fruit and berry crops. The calca­ reous chlorosis of plants thrives on carbonate soils, which contain from 10 to 50% and more carbonates [80]. In such soils at low pH, the plants are lacking iron and cannot form chlo­ rophyll. However, any soil always contains enough iron. The reason lies in the alkaline reaction of the soil, because there is too much lime, due to which iron is in an insoluble and hence, in an inaccessible form. Due to the lack of access to the plant organism, as well as the partial immobilization of iron already present in its tissues, a situation of deficiency of iron is created. In addition, chlorosis can be caused by the presence of high concentrations of metals such as Mn, Cu, Zn, Co, Ni or Cd, which can compete with Fe on the level of absorption by plants. The external manifestation of the phy­ siological changes caused by iron deficiency is chlorosis of leaves - a change in the color of leaves due to a decrease in the content of chlorophyll in them. When photosynthesis and respiration are impaired and weakened as a result of the insufficient formation of orga­ nic substances from which the plant's body is built, and the lack of organic reserves, a general metabolic disorder occurs. Therefore, with an acute lack of iron, the death of plants inevitably occurs. To protect against chlorosis caused by iron deficiency on carbonate soils, preparations containing iron in the form of complexonates are used [80–82]. The accepted mechanism for the treatment of iron chlorosis with iron che­ lates involves the enzymatic reduction of Fe3+ 125https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 to Fe2+ by the chelate of Fe(III) reductase. The result of this transformation is the release of Fe2+, which is absorbed by the roots, forming a free ligand molecule during the process. The effectiveness of iron chelate in solving the problem of chlorosis depends on several factors. The first is the ability of the organic compound to efficiently chelate Fe3+ and other metals present in soils (Ca2+, Mg2+ and Cu2+). Copper is normally present in soils in low con­ centrations, but becomes a major competitor to Fe3+ due to its ability to be chelated by amino acids. The second factor is the ability of plant roots to remove Fe3+ from the chelating agent. This ability is affected by the stability of Fe3+ and Fe2+ chelates. To predict the reactivity of iron chelates in plants and their effectiveness as chlorosis correctors, it is necessary to know the nature of the complexone and the stability of their complexes with iron, as well as to take into account their photochemical activity. In a series of polyaminocarboxylic complexes, stability increases in the order: FeNTA→ FeEDDHA→ FeEDDS→ FeEDTA→ FeDTPA. Therefore, the antichlorosis effect of more stable complexes is more effective than that of medium-resis­ tant chelates, and even more so of phosphonic complexes, which do not affect the synthesis of chlorophyll in iron-deficient leaves. Obviously, when phosphonic Fe-chelates are applied to the leaf surface, their photochemical inertness pre­ vents the formation of biologically active Fe(II) forms. In turn, the differences in the physiolog­ ical action between the photochemically active groups of moderately and highly stable Fe-che­ lates may be due to the unequal period of their photodecomposition. The best antichlorosis effect is possessed by iron complexes capable of intensive but prolonged photochemical de­ struction [49, 62, 67, 87]. The use of iron(III) complexes in vineyards showed that spraying grape plants affected by carbonate chlorosis and/or affected by freezing has a positive effect on the content of photo­ synthetic pigments in the leaves and increases the yield of plant berries [49, 61, 87, 90, 91]. Fertilization of chlorotic grape plants with FeEDTA and FeDTPA compounds not only increases the concentration of chlorophyll in leaves, but also reduces the content of organic acids compared to control plants. USE OF CHELATE COMPOUNDS OF MICRO ELEMENTS FOR PURIFICATION OF PLANTS AND SOIL FROM RADIONUC LIDES. Among the complex systems of mea­ sures aimed at minimizing the entry of radio­ nuclides from contaminated soil into the first link of the food chain – the plant, at present and probably in the coming decades, the most effective and economically justified system should be considered the use of mineral and organic fertilizers. When used purposefully in certain forms, quantities, ratios and combina­ tions, they can be used to reduce the input of radioactive substances to agricultural plants by many fold. After the accident at the Chornobyl nuclear power plant, the area most contaminat­ ed by radionuclides is the Ukrainian Polissia zone, which belongs to a biogeochemical pro­ vince, where soils, plants and, accordingly, fod­ der and products of plant and animal husband­ ry lack many biogenically important trace ele­ ments – iodine, zinc, manganese, cobalt, cop­ per, fluorine, lithium, boron and some others. This is the reason of the wide distribution of specific plant, animal and human diseases in this zone, which are known under the general name of hypomicroelement diseases (various forms of chlorosis, rosette leaves, small leafi­ ness in plants; hypocobaltosis, hypocuperosis, 126 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY keratosis, alimentary anemia in animals and humans) [92, 93]. Liming of acidic soils slows down the mobility and inhibits the transition from soil to plants not only of radionuclides, but also of other elements of mineral nutrition. But this is especially reflected in the content of trace elements. In [94] it was shown that under the influence of three times repeated liming of sod-podzolic soil at a dose of 2 t/ha with an interval of 4 years, the content of most of the listed microelements in oat and lupine plants decreased by almost half. It is known that some trace elements, including Zn, Mn, Co, Cu, have radioprotective properties, and some of them can affect the entry of radionuclides into plants and animals. Taking into account the situation with microelements in the region of Ukraine most contaminated with radionuclides, as well as their possible role in anti-radiation protec­ tion of living organisms, it is possible to pre­ dict their special role in the area affected by the accident. The radiosensitivity of most types of plants is quite high, so the damage from the accumulation of radionuclides by plants and their subsequent transport through food chains to animals and humans is a much more important problem than radiation damage to plants themselves. Therefore, the protective role of the factors that block the entry of radio­ nuclides into plants becomes a more important element of anti-radiation protection than the role of radioprotectors. It is indisputable that the basis of such blocking should be interac­ tions occurring between microelements and radionuclides. Various interactions are possible between trace elements and radionuclides: • additive, in which the effect of the compo­ nents is equal to the total sum of the effects of each component; • synergistic, when one of the components enhances the action of the other, as a result of which the physiological effect of their mixture exceeds the sum of the effects; • antagonistic, in which the effect of the ac­ tion is smaller than the action of each of the components separately and than the total ac­ tion [95, 96]. Additivity indicates the absence of inter­ action between elements. Antagonistic effect occurs in cases when one of the elements re­ duces the concentration of another or com­ petes with it for the places of absorption and further transport, but is unable to replace it in physiological processes. A synergistic ef­ fect is observed when one of the elements can partially replace the other in some functions (there can be no question of a complete re­ placement). Synergistic interaction can occur only in cases where an element is multifunc­ tional and can perform some functions to­ gether with other elements. On this basis, de­ pending on the conditions, which primarily include such indicators as the degree of radio­ nuclide pollution, the composition of radio­ nuclides, the granulometric composition of the soil, its agrochemical properties and some other indicators, three main strategies can be applied to reduce the degree of radionuclide entry into plants: 1. Creation of a competitive situation for the arrival of radionuclides on the basis of antago­ nistic interactions between them and elements of mineral nutrition; 2. Enhancement of the nutrient supply of ra­ dionuclide antagonists to plants, based on the synergism between individual elements and 3. Binding (complex formation) of radio­ nuclides in the soil using elements of mineral nutrition (Table 8). 127https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 Table 8. Possible interactions between macro- and microelements and Cesium-137 and Stron- tium-90. Antagonism Element Synergism B, Cu, F N B, Cu, Fe, Mo Al, As, B, Be, Ca, Cd, Cr, F, Fe, Hg, Mn, Mo, Ni, Pb, Sb, Si, Sr P B, Co, Cu, Mn, Mo, Zn Al, F, Cd, Cs, Hg, Mo, Rb, Se K B, Cu, Li, Mn, Zn Al, B, Ba, Cd, Co, Cs, Fe, Ns, Pb, Si, Sr Ca Cu, Li, Mn, Zn Al, B, Ba, Co, Cu, Cr, F, Fe, Mn, Ni, Zn Mg Al, Zn As, Ba, Fe, Mo, Pb, Se S F, Fe Ba, Ca, Cd, F, Fe, Mg, Li, Zn Sr Pb Cu, K, Li, Na Cs Cd, Ni It can be seen from table 8 that microele­ ments such as fluorine, iron, cadmium, lithium and zinc, and the macroelements – calcium, barium, magnesium can act as antagonists in relation to 90Sr. Lead is a synergist. In relation to 137Cs, microelements - copper and lithium, and macroelements – potassium and sodium act as antagonists. Synergists of radiocesium are cadmium and nickel. The given tabular data show the second possible relationship between microelements and radionuclides, when microelements contribute to the supply of macroelements to plants, and the latter, act­ ing as antagonists of radionuclides, affect the reduction of their supply to plants. The creation of a competitive situation be­ tween trace elements and radionuclides is based on the interaction of ions of elements with chemical properties close enough to com­ pete for absorption, transport and metabolism. At the same time, competition will be more significant for elements and radionuclides with similar sizes of ionic radii, charge, geometry of coordination and electronic configuration. The selection of antagonists can be carried out not only within one group of the periodic system, but also among the elements of other, as a rule, neighboring groups, among elements of varia­ ble valences. Research on the influence of trace elements on the uptake of radionuclides (137Cs, 90Sr) into plants was conducted mainly on contami­ nated soils in the northwestern part of Ukraine. A group of researchers under the leadership of Academician I.M. Gudkov. made a series of field experiments in the zone of Ukrainian Polissia to test the most promising trace elements: zinc, manganese, cobalt, copper, molybdenum, lithi­ um, boron and nickel [94, 97–100]. When se­ lecting them, a complex of indicators was taken into account: physiological role, deficiency in the environment, possible antagonistic inter­ actions with radionuclides, possible synergistic interactions with macroelements-antagonists of radionuclides, as well as radioprotective pro­ perties. The results of these studies indicate that, under the influence of trace elements, the accu­ mulation coefficients (Kaccum. – the ratio of the radionuclide content of plants to the content in the soil) of both radionuclides significantly 128 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY decreased both in comparison with the control without fertilizers and against the background of the main fertilizer (nitrogen-phosphate). The most effective trace element was zinc, un­ der the influence of which the KN in oat and lupine grains in the version without fertilizers decreased by 2–2.5 times. Manganese and co­ balt were somewhat less effective, copper, lithi­ um and boron were even less effective. It should be noted that the effectiveness of microelements was the greatest in the variants without fertili­ zers and the least against the background of in­ creased doses of fertilizers. This is quite natural, since, firstly, with fertilizers, a certain amount of the most diverse microelements is always in­ troduced into the soil in the form of impurities. And, secondly, in favorable conditions for the growth and development of plants, which are provided by fertilizers, the action of all factors, both positive and negative, is affected to a less­ er extent. When foliar feeding of plants (lupine, rapeseed, etc.) with aqueous solutions of zinc, manganese, cobalt, and copper sulfates in plants, the accumulation of 90Sr in the vegetative mass (straw) and seeds decreases by 25–40%, and 137Сs that of by 1.5 times [89 , 101–103]. Complexionates of microelements are much more effective in reducing the accumulation of radionuclides in plant products compared to their inorganic salts. Numerous works have shown that the treatment of various plants with complexonate solutions helps to reduce the specific radioactivity of both 137Cs and 90Sr by several times. For example, the work [104] presents the results of a three-year study the foliar fertilization of spring wheat crops of the Struna Myronivska variety with aqueous solu­ tions of zinc, manganese and their chelated analogues with EDTA in different phases of plant growth and development for the accu­ mulation of some trace elements in grain and straw. It was established that in the early phases of plant growth and development (spraying in the tillering phase), there is an increase in the concentration of both zinc and manganese at the time of harvesting in both grain and straw, but for the most part such growth does not in­ crease the yield of either grain or straw. In the case of foliar fertilization of wheat crops, espe­ cially with a zinc solution, the accumulation of iron, potassium, manganese, copper, zinc, and especially boron ions by plants from the soil increases by 1.5–2 times both in grain and in straw compared to the plants of the control variant. When feeding plants with a MnEDTA solution, a similar increase in the coefficients of accumulation of the specified microelements is observed. At the same time, the transition of 137Cs from the soil to grain decreases by 30– 35%. The highest effect of reducing the levels of contamination of wheat grain with radioce­ sium is observed when feeding plants with a solution of zinc complexonate in the first half of the growing season – in the phases of tiller­ ing and stooling. In [105] presents long-term studies on de­ termining the accumulation coefficients of 137Cs and 90Sr in the soil and grass of alpine pas­ tures in Switzerland. The long-term behavior of radionuclides was quantified using the ef­ fective half-life, which combines all processes that cause a decrease in activity in a given en­ vironment, such as leaching, fixation, erosion and radioactive decay. The results showed that 90Sr is more transferred from alpine soil to grass than 137Cs. This is explained by stronger fixation of Cs in soils. At the same time, the lower the concentration of calcium in the soil, the high­ er the absorption of 90Sr by grass. This is a very important fact, since it is traditionally believed 129https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 that radio-Sr, accumulating together with calci­ um in the skeleton, poses a threat only to blood cells. But it is well known that calcium is the main mineral component of plant cell mem­ branes and accumulates in increased amounts in the nuclear envelopes of all types of cells. Therefore, the high absorption of 90Sr by plants contributes to the purification of soils from ra­ dionuclide pollution, which is an integral part of phytoremediation. A similar conclusion can be drawn regarding radio-cesium. Thus, some microelements can block the transfer of radionuclides both from the soil to plants and from plants (forage) to the body of animals, thus reducing their accumulation in crop and livestock products. Microelements can influence certain aspects of metabolism in both plants and animals, the activity of metal-con­ taining enzymes, permeability of membranes. An intensive study of the effect of chelated microelements on reducing the accumulation of long-lived radionuclides 137Cs and 90Sr is be­ ing conducted at the Zhytomyr National Agro­ ecological University (from 2020, Polis Natio­ nal University) under the leadership of Ph.D of Agricultural Sciences V.M. Bidenko [106–112]. Chelated microfertilizers based on mono- and heterometallic complexonates with EDDS for field experiments were provided by a group of scientists of the Institute of General and Inor­ ganic Chemistry named after V.I. Vernadsky National Academy of Sciences of Ukraine. The effectiveness of microelement complexonates (Zn, Co, Mn, Cu) was determined under the conditions of field experiments on sod-podzo­ lic soils of the Zhytomyr region on various ag­ ricultural plants (wheat, rye, oats, corn, lupine, rapeseed, clover, etc.). The results of experi­ ments show that foliar feeding of lupine, vetch, clover, etc. plants with microelement complex­ onates helps to reduce the content of Cs-137 and Sr-90 in the green mass of the studied crops. For example, the 137Cs activity of lu­ pine green mass in the control was 671 Bq/kg, in the variants of using Mn and Zn sulfates, the 137Cs content was equal to ~ 440 Bq/kg, and in the areas where mono- and heterometallic complexes (ZnEDDS, MnEDDS, MnZnEDDS) were used, the 137Cs content was only ~350 and 260 Bq/kg, respectively. That is, microelement complexonates contributed to a decrease in the specific activity of Cs-137 by more than 50% (Fig. 14, a). Both microelements showed a high radio-blocking effect. Thus, zinc in the form of a salt solution reduced the accumulation of ra­ dio-cesium by more than 1.5 times), and in the form of ZnEDDS – by 2.1 times. The results of the action of trace elements on the accumula­ tion of 90Sr in plants were distinguished, first of all, by high coefficients of accumulation of the radionuclide (Kacum.=4.33). The influence of microelements in the form of salts on the accumulation of 90Sr in lupine plants was man­ ifested to a somewhat lesser extent compared to monometallic complexonates. The most ef­ fective data, as in the experiments with 137Cs, turned out to be in the version with the hete­ rometallic complex MnZnEDDS – the accu­ mulation of radio-strontium in the vegetative mass of lupine decreased by 34% (Fig. 14, b). It should be noted that microelements used as microfertilizers contributed to the activation of metabolic processes in plants through phyto­ hormones, enzymes, vitamins, improvement of metabolic processes in chlorophylls, contribut­ ing to the accumulation of metabolites in crops. In addition, under the influence of complexo­ nates, an increase in some microelements was observed in plants compared to the control: copper, zinc, iron and manganese [113]. 130 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY Fig. 14 – Influence of microelements and their complexonates on the accumulation of 137Cs and 90Sr in the lupine vegetative mass. 32 (ZnEDDS, MnEDDS, MnZnEDDS) were used, the 137Cs content was only ~350 and 260 Bq/kg, respectively. That is, microelement complexonates contributed to a decrease in the specific activity of Cs-137 by more than 50% (Fig. 14, a). Both microelements showed a high radio- blocking effect. Thus, zinc in the form of a salt solution reduced the accumulation of radio- cesium by more than 1.5 times), and in the form of ZnEDDS – by 2.1 times. The results of the action of trace elements on the accumulation of 90Sr in plants were distinguished, first of all, by high coefficients of accumulation of the radionuclide (Kacum.=4.33). The influence of microelements in the form of salts on the accumulation of 90Sr in lupine plants was manifested to a somewhat lesser extent compared to monometallic complexonates. The most effective data, as in the experiments with 137Cs, turned out to be in the version with the heterometallic complex MnZnEDDS – the accumulation of radio-strontium in the vegetative mass of lupine decreased by 34% (Fig. 14, b). Fig. 14 – Influence of microelements and their complexonates on the accumulation of 137Cs and 90Sr in the lupine vegetative mass. It should be noted that microelements used as microfertilizers contributed to the activation of metabolic processes in plants through phytohormones, enzymes, vitamins, improvement of metabolic processes in chlorophylls, contributing to the accumulation of metabolites in crops. In The obtained results confirm the opinion that one of the mechanisms of reducing the accumulation of 137Сs and 90Sr by plants under the influence of microelements can be due to the antagonistic interactions of microelements and the radionuclide on the one hand, and on the other hand, to an indirect effect due to the stimulation of the entry of macroelements into plants – its antagonists , in particular potassi­ um, calcium and possibly some other elements, a noticeable increase in the amount of which in plants was found during foliar treatments with zinc, cobalt and manganese. It is likely that the effect of the use of complexonates is associat­ ed with better penetration of the trace element through cell membranes, the ability to be di­ 131https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 rectly incorporated into the molecular struc­ tures of enzymatic systems, bypassing many transport chains. CONCLUSIONS. The role of trace elements in plant nutrition is multifaceted. In particular, Cu, Mo, Mn, Co, Zn, B and others increase the activity of many enzymes and enzyme systems in the plant body and improve the plant's use of nutrients from the soil and fertilizers. There­ fore, trace elements cannot be replaced by other substances, and their deficiency must be filled. Only then will we receive high-quality pro­ ducts that contain the optimal amount of su­ gars, amino acids, and vitamins for this vari­ ety. Microelements can accelerate plant deve­ lopment and seed ripening. They increase the resistance of plants to adverse environmental conditions (lack of moisture in the soil, increase or decrease in temperature). In addition, they protect plants from a number of bacterial and fungal diseases (bacteriosis of flax, beet heart rot, gray spotting of cereals, etc.), but unlike the effect of toxic chemicals, this occurs due to an increase in plant immunity. The scientifically justified use of microele­ ments in agricultural production is based not only on the need for them of a certain crop, but to a greater extent on their retention in the soil. It was established that the content of trace elements in the soil determines their content in plants, affecting their productivity and the quality of the yield. In this regard, the basis for the development of measures for the produc­ tion and use of microfertilizers should be the content of microelements in the soil, their ge­ ographical distribution and distribution along the soil profile. It has been established that trace elements in the form of inorganic salts work satisfactori­ ly only in acidic soils. In soils close to neutral, their effectiveness decreases tenfold. In neut­ ral, weakly alkaline and carbonate soils, inor­ ganic salts cannot retain microelements in a water-soluble form available to plants and their efficiency approaches zero, i.e. they turn into poorly soluble forms (hydroxide, carbonates) and become unavailable to plants. The researches of agrarian scientists and chemical scientists established that microele­ ments are most effective for plants in the form of metal complexes (chelates). In particular, the complexes are stable in all types of soil and there are no soil pH restrictions for them. It should be noted that the specific properties of various soils and the complex physiological processes occurring in the plant have a noticeable effect on the action of complex compounds. In this regard, it is difficult to assume the possibility of creating a universal means of combating the lack of trace elements on various soils. The most reliable solution to this problem is the creation of a wide range of metal chelates for their diffe­ rentiated application depending on the nature of the plant and the nature of the soil. In addition, the use of microelement com­ plexes can be an effective additional measure to reduce the ingress of radionuclides into ag­ ricultural plants, especially in biogeochemical provinces with their deficiency. AKNOWLEDGEMENT. The work was carried out with the financial support from the National Academy of Scien ces of Ukraine within the framework of the state budget topic «Creation of new hybrid, composite and polymer materials doped with coordination compounds of 3d- and 4f-metals based on beta-diketonate and carboxylate acyclic ligands.» The state regist ration number of the work is 0122U001299. 132 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY РОЛЬ ХЕЛАТНИХ КООРДИНАЦІЙНИХ СПОЛУК БІОГЕННИХ МЕТАЛІВ У ЖИТТЄДІЯЛЬНОСТІ РОСЛИН О. К. Трунова* Інститут загальної та неорганічної хімії ім. В. І. Вернадського НАН України, просп. Академіка Палладіна, 32/34, Київ 03142, Україна *e-mail: trelkon@gmail.com В оглядовій статті розглянуто основні питання створення та застосування су­ часних хелатних мікродобрив на основі мікроелементів у сільськогосподарському виробництві. Висвітлено питання ролі мік­ роелементів у життєдіяльності живих орга­ нізмів та способи подолання нестачі мікро­ елементів у рослинах. Представлено огляд координаційних сполук 3d-металів (Fe, Mn, Zn, Cu, Со, Ni, Mo) з різними класами комплексонів, особливості їхньої будови та властивостей. Міститься актуальний ма­ теріал про використання комплексонатів мікроелементів для створення сучасних хелатних добрив. Приділено увагу засто­ суванню комплексонатів мікроелементів на забруднених радіонуклідами (137Сs, 90Sr) територіях. Ключові слова: координаційні сполуки, мікроелементи, хелати, комплексони, доб­ рива, рослини. REFERENCES 1. Norrish K., Nicholas D.J.D., Egan A. R. The geo­ chemistry and mineralogy of trace elements, in Trace Elements in Soil-Plant-Animal Systems. Academic Press, New York. 1975. 55:432. 2. Kabata-Pendias A., Pendias H. Trace Elements in Soils and Plants. CRC рress (Boca Raton London, New York, Washington, D.C., 2001). 3. Ronen E. Micro-elements in agriculture. Practical Hydroponics and Greenhouses. 2016. (164): 35 4. Michalak I., Witek-Krowiak A., Chojnacka K., Bhatnagar A. Advances in biosorption of mic­ roelements–the starting point for the produc­ tion of new agrochemicals. Reviews in Inor- ganic Chemistry. 2015. 35 (3):115. https://doi.org/10.1515/revic-2015-0003 5. L´opez-Alonso M. Trace Minerals and Live­ stock: Not Too Much Not Too Little. Interna- tional Scholarly Research Notices. 2012. 2012: 1. https://doi.org/ 10.5402/2012/704825; 6. Thompson E. D., Hogstrand C., Glover C. N. From sea squirts to squirrelfish: facultative trace element hyperaccumulation in animals. Metallomics. 2018. 10 (6): 777. https://doi.org/10.1039/c8mt00078f. 7. Ivanishchev V.V. The role of iron in plant bio­ chemistry. News of the Tula state university. Natural sciences. 2019. (3): 149. [in Russian]. 8. Vigani G., Maffi D., Zocchi G. Iron availabili­ ty affects the function of mitochondria in cu­ cumber root. New Phytol. 2009. 182 (1): 127. https://doi.org/10.1111/j.1469-8137.2008.02 747.x. 9. Chatzistathis T. Physiological Importance of Manganese, Cobalt and Nickel and the Im­ provement of Their Uptake and Utilization by Plants. Plant Micronutrient Use Efficiency. 2018: 123–135. https://doi.org/10.1016/b978-0-12-812104-7. 00008-3. 10. Yeschenko V.O., Kopytko P.G., Opryshko V.P., Kostogryz P.V. Fundamentals of scienti 133https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 fic research in agronomy. Kyiv: Diya, 2005. [in Ukrainian]. 11. Makarova G.A., Lyubartsev V.M., Khonen­ ko L.G. The content and dynamics of mobile zinc and mobile manganese in the soils of the Mykolaiv region. Bull. Poltava state Agrarian academy. 2007. 1 (15): 60. [in Ukrainian]. 12. Hu X. Wei X., Ling J., Chen J. Cobalt: an essen­ tial micronutrient for plant growth? Frontiers in Plant Science. 2021. 2021: 2370. https://doi.org/10.3389/fpls.2021.768523. 13. Akeel A., Jahan A. Role of cobalt in plants: its stress and alleviation. Contaminants in agricul- ture - Springer, Cham. 2020: 339. https://doi.org/10.1007/978-3-030-41552-5_17. 14. Yruela I. Copper in plants. Brazilian Journal of Plant Physiology. 2005. 17 (1): 145.   https://doi.org 10.1590/s1677-0420200500010 0012/ 15. Printz B., Lutts S., Hausman J.-F., Sergeant K. Copper Trafficking in Plants and Its Implica­ tion on Cell Wall Dynamics. Frontiers in Plant Science. 2016. 7: 601. https://doi.org 10.3389/fpls.2016.00601. 16. Wairich A., De Conti L., Lamb T.І., Keil R., Neves L.O., Brunetto G., Sperotto R.A., Ricachenevsky F.K. Throwing Copper Around: How Plants Control Uptake, Distribution, and Accumula­ tion of Copper. Agronomy. 2022. 12 (5): 994. https://doi.org/10.3390/agronomy12050994. 17. Alloway B. J. (Ed.). Micronutrient deficiencies in global crop production. Springer Science & Business Media. 2008. 18. Laporte D., Rodríguez F., González A., Zúñi­ ga A., Castro-Nallar E., Sáez C. A., Moenne A. Copper-induced concomitant increases in photosynthesis, respiration, and C, N and S as­ similation revealed by transcriptomic analyses in Ulva compressa (Chlorophyta). BMC plant biology. 2020. 20 (1): 1. https://doi.org/10.1186/s12870-019-2229-5. 19. Belchhazy V., Dankanych T.Influence of cop­ per on growth and development of grapes Bull. Uzhgorod Univ. (Ser. Biol.) 2011. 30: 164. [in Ukrainian]. 20. Mir A. R., Pichtel J., Hayat S. Copper: uptake, toxicity and tolerance in plants and manage­ ment of Cu-contaminated soil. Biometals. 2021. 34 (4): 737. https://doi.org/ 10.1007/s10534-021-00306-z. 21. Kaiser B.N., Gridley K.L., Ngaire Brady J. Phil­ lips T., Tyerman S.D. The role of molybdenum in agricultural plant production. Annals of bo tany. 2005. 96 (5): 745. https://doi.org/ 10.1093/aob/mci226. 22. Mendel R.R., HaÈnsch R. Molybdoenzymes and molybdenum cofactor in plants. Journal of experimental botany. 2002. 53 (375): 1689. https://doi.org/ 10.1093/jxb/erf038. 23. Min Y.U., Hu C.X., Sun X.C., Wang Y.H. In­ fluences of Mo on nitrate reductase, glutamine synthetase and nitrogen accumulation and utilization in Mo-efficient and Mo-inefficient winter wheat cultivars. Agricultural Sciences in China. 2010. 9 (3): 355. https://doi.org/10.1016/S1671-2927(09)6010 4-8. 24. Rana M. S., Bhantana P., Imran M., Saleem M. H., Moussa M. G., Khan Z., Hu C. Molyb­ denum potential vital role in plants metabo­ lism for optimizing the growth and develop­ ment. Annals of Environmental Science and Toxicology. 2020. 4 (1): 32. 25. Manuel T.-J., Alejandro C.-A., Angel L., Auror G., Emilio F. Roles of Molybdenum in Plants and Improvement of Its Acquisition and Use Efficiency. Plant Micronutrient Use Efficiency, 2018.: 137. https://doi.org/10.1016/b978-0-12-812104-7. 00009-5 26. Mishra D., Kar M. Nickel in plant growth and metabolism. The botanical review. 1974. 40 (4): 395. 27. Fabiano C.C., Tezotto T., Favarin J.L., Po­ lacco J.C., Mazzafera P. Essentiality of nickel in plants: a role in plant stresses. Frontiers in plant science. 2015. 6: 754. https://doi.org/ 10.3389/fpls.2015.00754. 28. deCatanzaro J.B., Hutchinson T.C. Effects of nickel addition on nitrogen mineralization, 134 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY nitrification, and nitrogen leaching in some boreal forest soils. Water, Air, and Soil Pollu- tion, 1985. 24 (2): 153. 29. Dalton D.A., Evans H.J., Hanus F.J. Stimula­ tion by nickel of soil microbial urease activity and urease and hydrogenase activities in soy­ beans grown in a low-nickel soil.  Plant and Soil. 1985. 88 (2): 245. 30. Cataldo D. A., Garland T.R., Wildung R.E. Nickel in plants: I. Uptake kinetics using intact soybean seedlings. Plant Physiology. 1978. 62 (4): 563. https://doi.org/ 10.1104/pp.62.4.563. 31. Tiffin L.O. The form and distribution of metals in plants: an overview. In  Biological implica- tions of metals in the environment. TIC, Oak Ridge, 1977. TN, CONF-750929. 32. Küpper H., Kroneck, P. M. Nickel in the en­ vironment and its role in the metabolism of plantsand cyanobacteria. Metal Ions in Life Sciences. 2007. 2: 31–62. https://doi.org/10.1002/9780470028131.ch2, 33. Polacco J.C., Mazzafera P., Tezotto T. Opi­ nion–nickel and urease in plants: still many knowledge gaps. Plant Science. 2013. 199: 79. https://doi.org/10.1016/j.plantsci.2012.10.010. 34. Rodríguez-Jiménez T.D.J., Ojeda-Barrios D.L., Blanco-Macías F. Valdez-Cepeda R.D., Parra- Quezada R. Urease and nickel in plant physio­ logy.  Revista Chapingo. Serie horticultura. 2016. 22 (2): 69. https://doi.org/10.5154/r.rchsh.2014.11.051. 35. Rechenmacher C., Wiebke-Strohm B., Olivei­ ra-Busatto L.A.D., Polacco J.C., Carlini C.R., Bodanese-Zanettini M.H. Effect of soybean ureases on seed germination and plant deve­ lopment. Genetics and molecular biology. 2017. 40: 209. https://doi.org/10.1590/1678-4685-gmb- 2016-0107. 36. Yusuf M., Fariduddin Q., Hayat S., Ahmad A. Nickel: an overview of uptake, essentiality and toxicity in plants.  Bulletin of environmental contamination and toxicology. 2011. 86 (1): 1. https://doi.org/10.1007/s00128-010-0171-1. 37. Gajewska E., Wielanek M., Bergier K., Skło­ dowska M. Nickel induced depression of ni­ trogen assimilation in wheat roots. Acta Phy siologiae Plantarum. 2009. 31: Р. 1291. https://doi.org/10.1002/clen.200800199. 38. Nishida S., Tsuzuki C., Kato A., Aisu A., Yoshi­ da J., Mizuno T. AtIRT1, the primary iron up­ take transporter in the root, mediates excess nickel accumulation in Arabidopsis thaliana. Plant and Cell Physiology. 2011. 52 (8): 1433. https://doi.org/ 10.1093/pcp/pcr089. 39. Shahzad B., Tanveer M., Rehman A., Cheema S.A., Fahad S., Rehman S., Sharma A. Nickel; whether toxic or essential for plants and envi­ ronment-A review.  Plant Physiology and Bio- chemistry. 2018. 132: 641. https://doi.org/10.1016/j.plaphy.2018.10.014. 40. Sanin Yu.V. Sanin V.A., Sanin O.Yu., Peculiari­ ties of foliar feeding of agricultural crops with trace elements. Agronomist. 2016. (4): 36. [in Ukrainian]. 41. Bailar J.C. Some Coordination Compounds in Biochemistry: A review of the role of metal ions in life processes. American Scientist. 1971. 59 (5): 586. 42. Haas K.L., Franz K.J. Application of metal co­ ordination chemistry to explore and manipu­ late cell biology. Chemical reviews. 2009. 109 (10): 4921. https://doi.org/10.1021/cr900134a. 43. Malinowski J., Zych D., Jacewicz D., Gawdzik B., Drzeżdżon J. Application of coordination com­ pounds with transition metal ions in the chemi­ cal industry—A review. International Journal of Molecular Sciences. 2020. 21 (15): 5443. https://doi.org/10.3390/ijms21155443. 44. O'Halloran T.V., Culotta V. C. Metallochape­ rones, an intracellular shuttle service for metal ions. J. Biological Chemistry. 2000. 275 (33): 25057. https://doi.org/10.1074/jbc.R000006200. 45. Jeevanandam J., Barhoum Ah., Chan Yen S, Dufresne A., Danquahcorresponding M. Re­ view on nanoparticles and nanostructured materials: history, sources, toxicity and regu­ lations Beilstein. J. Nanotechnol. 2018. 9: 1050. 135https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 https://doi.org/10.3762/bjnano.9.98. 46. Li X., Wang L., Fan Y., Feng Q., Cui F. (Biocom­ patibility and Toxicity of Nanoparticles and Na­ notubes. J. Nanomaterials. 2012. 2012: 1. https://doi.org/10.1155/2012/548389. 47. Klüner T., Hempel D.C., Nörtemann B. Meta­ bolism of EDTA and its metal chelates by whole cells and cell-free extracts of strain BNC1. Applied microbiology and biotechnolo- gy. 1998. 49 (2): 194. 48. Race M., Ferraro A., Fabbricino M., La Mar­ ca A., Panico A., Spasiano D., ... Pirozzi F. Ethy­ lenediamine-N, N′-disuccinic acid (EDDS)  – enhanced flushing optimization for contami­ nated agricultural soil remediation and assess­ ment of prospective Cu and Zn transport. In- ternational journal of environmental research and public health. 2018. 15 (3): 543. https://doi.org/10.3390/ijerph15030543. 49. Dyatlova N.M. Theoretical foundations of the action of complexones and their applica­ tion in the national economy and medicine. ZhVHO im. D.I. Mendeleeva. 1984. 29 (3):7. ISSN 0373-0247. [in Russian]. 50. Kramarev S., Artemenko S. Chelated fertili­ zers and their prospects. Zhurnal suchasnogo agropromislovtsya. Zerno. 2012. (1): 24. [in Ukrainian]. 51. Trunova E.K., Dudko A.V., Osadsha E.V., Shovkova A.V., Makotryk T.A. Poly [[diaqua [μ5-(R, S)-2-({2-[(1, 2-dicarboxylatoethyl) amino] ethyl} amino) butanedioato] cobaltate (III) sodium] dihydrate]. Acta Crystallographi- ca Section E: Structure Reports Online. 2011. 67 (11): 1547.   https://doi.org/10.1107/S160053681104013X 52. Harvey L. Mineral bioavailability. Nutrition & Food Science. 2001. 31 (4):179. https://doi.org/10.1108/00346650110392253. 53. Sekhon B. S. Chelates for micronutrient nutri­ tion among crops. Resonance. 2003. 8 (7): 46. https://doi.org/10.1007/BF02834402. 54. Yiannikouris A., Connolly C., Power R., Lo­ binski R. Characterization of metal–peptide complexes in feed supplements of essential trace elements. Metallomics. 2009. 1:.235. https://doi.org/10.1039/B901406C. 55. YuntaF., García-Marco S., Lucena J. J., Gómez- Gallego M., Alcázar R., Sierra M. A. Chelating agents related to ethylenediamine bis (2-hy­ droxyphenyl) acetic acid (EDDHA): synthe­ sis, characterization, and equilibrium studies of the free ligands and their Mg2+, Ca2+, Cu2+ and Fe3+ chelates. Inorganic chemistry. 2003. 42 (17): 5412. https://doi.org/10.1021/ic034333j. 56. Loginova E.S., Nikolskii V.M., Tolkache­ va L.N., Lukyanova N.I. synthesis and some properties of complexones, succinic acid de­ rivatives. Russian Chemical Bulletin, Interna- tional Edition. 2016. 65 (9): 2206. https://doi.org/1066-5285/16/6509- 2206. 57. Asemave K. Greener chelators for recovery of metals and other applications.  Org. Med. Chem. Int. J. 2018. 6 (4): 555694..   https://doi.org/10.19080/OMCIJ.2018.06.55 5694. 58. Geiger E.Yu., Varlamova L.D., Semenov V.V., Pogodina Yu.V., Sirotina Yu.A. Microfertilizers on a chelate basis: experience and prospects for use. Agrochemical Bulletin. 2017. (2): 29. [in Russian]. 59. Mazurenko Y., Rogovtsov A., Trunova E., Gera­ simchuk A. The direct fragmentation of com­ plexonates Mn (II) and Ce (III) with ethylene diamine disuccinic acid. Ukr. Chem. J., 2000. 66 (11): 76. 60. Trunova E., Rogovtsov A., Mazurenko E., Shte­ menko N., Makotrik T. Photochemical activity of complexes of Mn(II) with ethylenediamine­ disuccinic acid. Ukr. Chem. J. 2001. 67 (1): 7. 61. Trunova O.K. Biologically active complexes of ethylenediaminedisuccinic acid with 3d-met­ als. (Synthesis, structure, properties). Doctoral (Chem.) Thesis (Kyiv, 2012) [in Ukrainian]. 62. Bityutsky N.P. Trace elements and plants. St. Petersburg: Publishing House of St. Peters­ burg. un-ta, 1999. ISBN 5-288-02212-7. [in Russian]. 63. Koolman J., Roehm K.-H. Visual biochemistry. (Moscow: Knowledge Lab, 2021). 136 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY ISBN 978-5-00101-311-2. [in Russian]. 64. Nelson D.L., Cox M.M. Lehninger Principles of biochemistry. (New York: W.H. Freeman and company, 2008). ISBN 978-0-7167-7108-1. 65. Bulygin S.Yu., Demishev L.F., Doronin V.A., Zarishnyak A.S., Pashchenko Ya.V., Turovsky Yu.E., ... Yakovenko M.M. Microelements in agriculture. (Dnipropetrovsk: Sich, 2007). ISBN 978-966-511-306-2 [in Russian]. 66. Wallace A. General conclusions concerning chelating agents in plant nutrition in 1982. J. Plant. Nutr. 1983. 6 (3): 425. https://doi.org/10.1080/01904168309363104. 67. Ostrovskaya L.K. Complexons and their im­ portance for plant nutrition with trace metals. Physiology and biochemistry cult. Plants. 1986. 18 (6): 591. [in Russian]. 68. Nikolsky V.M., Pchelkin P.E., Sharov S.V., Knya­ zeva N.E., Gorelov I.P. Synthesis and application of complexones, derivatives of succinic acid, in industry and agriculture. Successes of Modern Natural Science. 2004. (2): 71. [in Russian]. 69. Molassiotis A.N., Dimassi K., Therios I., Dia­ mantidis G. Fe-EDDHA promotes rooting of rootstock GF-677 (Prunus amygdalus× P. persica) explants in vitro. Biologia Plantarum. 2003. 47 (1): 141. https://doi.org/10.1023/A:1027309705022. 70. Kudryashova N.V., Sharov S. V., Nikolsky V. M., Gorelov I. P. Ecologically pure complexons for regulation of plant growth and develop­ ment. New advances in chemistry and chemical technology of plant raw materials. 2005. 661. 71. Molassiotis A. N., Dimassi K., Therios I., Di­ amantidis G. Fe-EDDHA promotes rooting of rootstock GF-677 (Prunus amygdalus×P. persica) explants in vitro. Biologia Plantarum. 2003..47 (1): 141. https://doi.org/10.1023/A:1027309705022 72. Mazurenko E.A., Trunova E.K. Biologically active complexes based on succinic acid. Ukr. Chem. J. 2001. 67 (7): 24. [in Russian]. 73. Seifullina I.I., Pesaroglo А.G., Martsinko E.E., Chebanenko E.A., Pozharitskiy A.P. Synthesis and structure of the magnesium 1-hydroxy­ ethilidendiphosphonatogermanat(IV), its in­ fluence on the growth and development of winter wheat. Odesa National University He rald Chemistry. 2019. 25 (1(69)):6. https://doi.org/10.18524/2304-0947.2019. 1(69).158415. 74. Nikulina E.A., Akimova S.V., Tsirulnikova N.V., Glinushkin A.P., Dolgoborodov I.O., Kirkach V.V. Screening of different Fe (II) and Fe (III) complexes at the stage of rhizogenesis in vitro of gooseberry plants. In Journal of Physics: Con- ference Series. 2021. 1942 (1): 012075. https://doi.org/10.1088/1742-6596/1942/1/ 012075. 75. Tananayeva N.M., Kostromina N.A., Trunova O.K., Zhigadlo B.A., Strashko V.V., Horokho­ vatska M.Ya. The method of obtaining a growth stimulator of buckwheat plants based on a complex compound of iron (III). Ukrai­ nian patent № 100305, 1997. [in Ukrainian]. 76. Kostromina N.A., Tananayeva N.M., Zhigad­ lo B.A., Horokhovatska M.Ya. Fertilizer for alfalfa plants. Author's certificate of the USSR № 3444313/30-15, 1983. [in Russian]. 77. Geiger E.Yu., Varlamova L.D., Semenov V.V., Pogodina Yu.V., Sirotina Yu.A. Microfertilizers on a chelate basis: experience and prospects for use. Agrochemical Bulletin. 2017. 2 (2): 29. [in Russian]. 78. Albano J.P., Merhaut D.J. Influence of FeEDDS, FeEDTA, FeDTPA, FeEDDHA, and FeSO4 on Marigold Growth and Nutrition, and Substrate and Runoff Chemistry. Hort. Science. 2012. 47 (1): 93. https://doi.org/10.21273/HORTSCI.47.1.93 79. Albano J.P. Effects of FeEDDS and EDDS on Peat-based Substrate pH and Cu, Fe, Mn, and Zn Solubility. Hort. Science. 2012. 47 (8): 269. https://doi.org/10.21273/HORTSCI.47.2.269. 80. Gonzalez D., Obrador A., Alvarez J.M. Behavior of Zinc from Six Organic Fertilizers Applied to a Navy Bean Crop Grown in a Calcareous Soil. J. Agric. Food Chem. 2007. 55 (17): 7084. https://doi.org/10.1021/jf071090v. 81. Nikolsky V.M., Smirnova T.I., Pastushenkov Yu.G., Skokov K.P. Effect of biologically active complexones, derivatives of dicarboxylic acids, 137https://ucj.org.ua O. K. Trunova UCJ № 12 / Vol. 88 and magnetic field on the content of plant pigments in spinach. Bulletin of the Tver State University. Series: Biology and Ecology. 2007. (6): 80. ISSN 1995-0160. [in Russian]. 82. Wei L., Luo C., Wang C., Li X., Shen Z. Biode­ gradable chelating agent ethylenediaminedi­ succinic acid reduces uptake of copper through alleviation of copper toxicity in hydroponical­ ly grown Chrysanthemum coronarium L. En- vironmental Toxicology and Chemistry: An In- ternational Journal. 2007. 26 (4): 749 https://doi.org/10.1897/06-409r1.1. 83. Smirnova T.I., Smirnova O. V. Influence of complexones, derivatives of succinic acid, and their borate complexes on soil microflora. Bul- letin of the Tver State University. Series: Che mistry. 2015. (3): 40. [in Russian]. 84. Ivanyutina N. N., Smirnova T. I., Drozdov I. A. Changes in protein content in wheat grain under the action of magnesium and zinc com­ plexonates. Bulletin of the Tver State University. Series: Chemistry. 2016. (1): 110. [in Russian]. 85. Trunova E.K., Mazurenko E.A., Makotryk T.A., Rogovtsov A.A. One-step synthesis of biologically active complexes of 3d metals. Reports of the National Academy of Sciences of Ukraine. 2002. (12): 124. [in Russian]. 86. Trunova E.K., Mazurenko E.A., Rogovtsov A.A. New ecologically pure complexon as a chelating reagent. Application in various fields of industry. Chemical Industry. Ukraine. 2006. (5): 19. [in Russian]. 87. Shadchyna T.M., Priadkina G.O., Trunova O.K. Antichlorosis properties of microelement complexes (iron and copper). Physiology and Biochemistry of Cultivated Plants. 2008. 40 (5): 435. [in Ukrainian]. 88. Bereghnytska O. S., Trunova E. K., Makotrik T. A., Grusha V.V. Heterometal complexes of Zn(II) and Mn(II) with biological active com­ plexones.  Ukr. Chem. J. 2004. 70 (9): 12. [in Ukrainian]. 89. Gudkov I.M., Grusha V.V., Grysyuk S.M., Tru­ nova O.K., Rogovtsov O.O. Effectiveness of foliar fertilization of lupine and rapeseed with trace elements complexonates in reducing the accumulation of radionuclides and increasing plant productivity. Scientific Bulletin of NAU. 2004. (79): 233. [in Ukrainian]. 90. Bavaresco L., Fregoni M., Fogher С. Effects of some biological methods to improve Fe - ef­ ficiency in grsffed grapevine. Iron nutrition in Soil and Plants. 1995. 59: 81. ISBN:978-94-010-4224-6 91. Natt C. Effect of slaw releaze ironfertilizers on chlorosis in grape. J.Plant nutritions. 1992. 15 (10):1891. https://doi.org/10.1080/01904169209364446. 92. Gudkov I.M., Vinnichuk M.M. Agricultural radiobiology. (Zhytomyr: State Agroecological Academy of Ukraine, 2003). [in Ukranian]. 93. Vinichuk M.M., Rosén K. Cesium (137Cs and 133Cs) and Selected Metals in the Environment. (Publisher: Science Publishing Group, 2015). [In English]. 94. Gudkov I.M., Grysiuk M.S., Kitsno V.O. Re­ duction of 90Sr and Cs into agricultural plants under the influence of trace elements. Scienti fic Bulletin of the National Agrarian University. 1998. (10): 264. [in Ukranian]. 95. Gudkov I.M. Radiobiology. (Kyiv: National University of Life and Environmental Sciences of Ukraine , 2016, ]. [in Ukranian]. 96. Gudkov I.N., Lazarev N.M., Grusha V.V., Bi­ denko V.N. The role of trace elements in radi­ ation protection of plants and animals on ra­ dionuclide contaminated territories of Poles'e. Radiatsionnaia Biologiia, Radioecologiia. 2011. 51 (1): 33. PMID: 21520614. 97. Grodzinskyi D.М., Bulakh А.А., Gudkov І.М. Radiobiological effects in plants. Chornobyl ca- tastrophe. (Кyiv: Naukova dumka, 1996.) [in Ukranian]. 98. Grodzinsky D.M., Gudkov I.N. Radiation da mage of plants in the Chernobyl Nuclear Acci- dent impact zone. 20 Years After the Chernobyl Accident: Past, Present and Future. (New York: Nova Science Publishers, 2006). 99. Gudkov I.M., Grodzinskyi D.M. Peculiarities of formation of absorbed doses and distant radiobiological effects in agricultural plants in territories contaminated with radionuclides. 138 ISSN 2708-129X. Укр. хім. журн., 2022 THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS.INORGANIC CHEMISTRY Bulletin of DAAU. 2001. (1): 8. [in Ukranian]. 100. Gudkov I.M., Grodzinskyi D.M. Radiation damage to plants in the zone affected by the accident at the Chornobyl NPP. Herald of Agrarian Science, Special issue. April 2001.: 43. [in Ukranian]. 101. Grusha V.V., Gudkov I.N. Influence of foliar fertilization of plants with trace elements on accumulation of 137Cs. Scientific Bulletin of NAU. 2003. (63): 263. [in Ukrainian]. 102. Grusha V.V., Gudkov I.N. Zn and Mn micro­ elements action on the accumulation radionu­ clides 137Сs and 90Sr decreasing and on pro­ ductivity of plants. Sci. Bull. Uzhgorod Univ. (Ser. Biol.). 2008. 24: 149. [in Ukranian]. 103. Grusha V.V., Gudkov I.N. The effect of Zn and Mn compounds on reducing the intake of ra­ dionuclides ¹³⁷Сs and ⁹⁰Sr and plant produc­ tivity. Bulletin of the Zhytomyr National Agra rian University. 2009. (2): 48. [in Ukranian]. 104. Vinichuk M.М., Mandro Yu.N. Translocation of some of the microelements within grain and straw of spring wheat of the Struna Mironovs’ka variety after foliar fertilization on soils contami­ nated by radionuclides. Environmental sciences. 2021. 7 (34): 167. [in Ukranian]. https://doi.org/10.32846/2306-9716/2021.eco. 7-34.28. 105. Corcho-Alvarado J.A., BalsigerB., Sahli H., Astner M., Byrde F., Röllin S., ... Burger M. Long-term behavior of 90Sr and 137Cs in the en­ vironment: case studies in Switzerland. Journal of environmental radioactivity. 2016. 160.: 54. https://doi.org/10.1016/j.jenvrad.2016.04.027. 106. Bidenko V.M., Kurachenko N.M., Trunova O.K., Lavreniuk O.O., Osadcha O.V. Radio-eco­ logical and productive assessment of the use of microelement complexes in the cultivation of fodder crops of the "Polyssya" STOV of the Na­ rodnytsky District. Bulletin of the State Agroeco- logical University. 2008. (1): 49. [in Ukranian]. 107. Bidenko V. M., Lavrynyuk O. O., Rudyk R. I., Kurachenko N. M., Osovets Yu. V. Effective­ ness of using complexonates of microelements Co, Su, Ζn, Mn when growing red clover for green fodder. Fodder and fodder production. 2008. (62):144. [in Ukranian]. 108. Bidenko V.M., Trunova O.K., Kurachenko N.M., Shubenko O.I. The effectiveness of the use of trace elements complexonates in order to reduce the accumulation of 137Cs and 90Sr in the green mass of vetch. Collection of scientific works of Vinnytsia State. Agrarian University. 2008. 2 (34): 100. [in Ukranian]. 109. Bidenko V., Slavov V., Trohumenko V., Kal­ chyk L. Radioactivity and Yield of Leguminous Fodder Crops in its Feeding by Complexonates of Microelements. Agrobiodiversity for improv- ing nutrition, health and life quality : scientific proceedings. Nitra : Slovak university of agricul- ture in Nitra. 2016.: 30. [in Ukranian]. 110. Bidenko V.N., Slavov V.P., Trochimenko V.Z. The effectiveness of the use of salts and com­ plexonates of microelements for growing legu­ minous fodder crops in the zone of radioac­ tive contamination. Tauride scientific observer. 2016. 5-2 (10): 239. [in Russian]. 111. Bidenko V.M., Slavov V.P., Didukh M.I., Kal­ chuk L.A., Trochymenko V.Z. The effectiveness of the use of various compounds of microele­ ments in the cultivation of fodder lupine in the conditions of the zone of radioactive contami­ nation. Bulletin of Sumy National Agrarian University, Series: Livestock. 2018 (2): 129. [in Ukranian]. 112. Bidenko V.M., Kalchuk L.A., Trochymenko V.Z. Effectiveness of Usage of Salts and Com­ pounds of Microelements in The Growth of Lupin on Radioactive Contaminated Soils Podilian Bulletin Agriculture Engineering Eco- nomics. 2019. 1 (30): 9. https://doi.org/10.37406/2706-9052-2019-1-1. 113. Bidenko V.M., Mamchenko V. Yu., Kovalchuk T.I. Influence of various microelement com­ pounds on yield, nutritional value and accu­ mulation of 137Cs in green mass of oats. Bulle- tin of Sumy National Agrarian University. 2021. 4 (47): 60. https://doi.org/10.32845/bsnau.lvst.2021.4.10. Стаття надійшла 07.01.2023.
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spelling oai:ojs2.1444248.nisspano.web.hosting-test.net:article-5052026-07-22T08:23:50Z THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS Trunova, Olena coordination compounds, microelements, chelates, complexones, fertilizers, plants. The review article discusses the main issues of creating and using modern chelated microfertilizers based on trace elements in agricultural production. Issues of the role of microelements in the vital activity of living organisms and methods of overcoming the lack of micro­elements in plants are highlighted. An overview of coordination compounds of 3d-metals (Fe, Mn, Zn, Cu, Co, Ni, Mo) with different classes of complexons, features of their structure and properties is presented. It contains relevant material on the use of microelement complexes for the creation of modern chelated fertilizers. Attention is paid to the use of trace elements complexonates in areas contaminated with radionuclides (137Сs, 90Sr). V.I.Vernadsky Institute of General and Inorganic Chemistry 2023-01-27 Article Article Inorganic Chemistry Неорганическая химия Неорганічна хімія application/pdf https://ucj.org.ua/index.php/journal/article/view/505 10.33609/2708-129X.88.12.2022.91-138 Ukrainian Chemistry Journal; Vol. 88 No. 12 (2022): Ukrainian Chemistry Journal; 91-138 Украинский химический журнал; ##issue.vol## 88 ##issue.no## 12 (2022): Ukrainian Chemistry Journal; 91-138 Український хімічний журнал; Том 88 № 12 (2022): Український хімічний журнал; 91-138 2708-129X 2708-1281 en https://ucj.org.ua/index.php/journal/article/view/505/257 Copyright (c) 2023 Olena Trunova https://creativecommons.org/licenses/by-nc/4.0
spellingShingle Trunova, Olena
THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS
title THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS
title_full THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS
title_fullStr THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS
title_full_unstemmed THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS
title_short THE ROLE OF CHELATE COORDINATION COMPOUNDS OF BIOGENIC METALS IN THE VITAL ACTIVITY OF PLANTS
title_sort role of chelate coordination compounds of biogenic metals in the vital activity of plants
topic_facet coordination compounds
microelements
chelates
complexones
fertilizers
plants.
url https://ucj.org.ua/index.php/journal/article/view/505
work_keys_str_mv AT trunovaolena theroleofchelatecoordinationcompoundsofbiogenicmetalsinthevitalactivityofplants
AT trunovaolena roleofchelatecoordinationcompoundsofbiogenicmetalsinthevitalactivityofplants