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International Journal of Trend in Scientific Research and Development (IJTSRD)
Volume 4 Issue 6, September-October 2020 Available Online: www.ijtsrd.com e-ISSN: 2456 – 6470
@ IJTSRD | Unique Paper ID – IJTSRD33515 | Volume – 4 | Issue – 6 | September-October 2020 Page 901
Role of Copper in Environment as a Potential and Challenges
Dharmpal Meet A1, Rathod Zalak R2
1Department of Biotechnology, Kadi Sarva Vishwavidyalaya, Gandhinagar, Gujarat, India
2Department of Microbiology and Biotechnology, University School of Sciences,
Gujarat University, Ahmedabad, Gujarat, India
ABSTRACT
Copper is a normally mixing component. Present in the world's shell, in seas,
lakes and waterways, wellsprings of copper extend from minute follow sums
to rich mine stores. Copper is a fundamental component, implying that all
plants, fish and creatures need copper to work appropriately. All around the
market for copper is one of the biggest of all metals following iron and
aluminium. Copper can be delivered into the earth by both characteristic
sources and human exercises. Present day life has various applications for
copper, extending from coins to colours, and interest for the metal stays high,
particularly in industrialized countries.
KEYWORDS: Copper; Microbes; Iron; Aluminium; Metal
How to cite this paper: Dharmpal Meet A
| Rathod Zalak R "Role of Copper in
Environment as a Potential and
Challenges"
Published in
International Journal
of Trend in Scientific
Research and
Development(ijtsrd),
ISSN: 2456-6470,
Volume-4 | Issue-6,
October 2020, pp.901-903, URL:
www.ijtsrd.com/papers/ijtsrd33515.pdf
Copyright © 2020 by author(s) and
International Journal ofTrendinScientific
Research and Development Journal. This
is an Open Access article distributed
under the terms of
the Creative
CommonsAttribution
License (CC BY 4.0)
(http://creativecommons.org/licenses/by/4.0)
INTRODUCTION
Copper is a naturally stirring element. Present in the earth’s
shell, in oceans, lakes and rivers, sources of copper range
from minute trace amounts to rich mine deposits. Copper is
an essential element, meaning that all plants, fish and
animals need copper to function properly.
(copperalliance.eu) Copper contamination is one of the
major environmental hazards in contaminated areas
(Chaney et al., 1997). Normal concentration of copper in
plant tissues is approximately 5-25 mg/kg. Copper toxicity
due to many aspects of its behaviour inhibits iron
metabolism and the activities of many enzymes (Hou et al.,
2007). Universally the market for copperisoneofthelargest
of all metals following iron and aluminium. The size of the
largely market for developed copper is over U$149 billion
every year, Copper has been a material component in the
growth of human civilizationsforthousandsofyears.India is
one of the top 20 major producers ofcopperuniversally.Asa
result, instability in prices of the metal on the LME has an
important bearing on Indian copper trading. Over 30% of
India‘s copper demand comes from the telecom sector and
26% from the electrical sector. In addition, the building and
construction, engineering, transportandconsumerdurables
sectors are major consumers of copper in India. (Kabwe;
Yiming, 2015)
Environmental form of copper
Copper occurs in the soil almost excl suavely in divalent
form. The largest fraction of Cu is usually present in the
precious stone latticesofprimaryandsecondaryminerals.In
addition a high fraction of Cu is bound by the soil organic
matter. The Cu ion is adored to inorganic and organic
negatively charged groups and is dissolved in the soil way
out as Cu2 + and organic Cu complexes. Copper is specifically
adsorbed to carbonates, soil organic matter, phyllo silicates,
and hydrous oxides of AI, Fe, and Mn. (Reed; Martens, 1996)
The focus of Cu2 + in the soil solution decreases sharplywith
an increasing pH where as the concentration of organic Cu
complex in the soil explanation is less dependent on soil pH.
Higher pH may even promote the termination of organic Cu
complexes. The divalent Cu ion has a strong affinity to soil
organic matter compared with other divalent cations as is
shown by the following sequence (Schnitzer, 1965; Skinner,
1967): Cu > Ni > Pb > Co > Ca > Zn > Mn > Mg Copper may be
bound in chelated form to organic matter which means that
it is held by covalent and coordinative bonds. It is
coordinatively bound to 0, N, and S atoms following the
preference S > N > O. Since N is present in soil organic
material in much higher concentrations than S, N atomstake
part in the major role in chelating Cu2+ inquantitativeterms.
Recent findings indicate that a large proportion of Cu2+ is
also bound covalently to carboxylic groupsasoccurinhumic
and fulvic acids in soil organic matter and as shown below.
This is covalent mono dentate binding of Cu2 + to the
carboxylic group R-COO- + Cu2+= R-COO Cu+ is not as strong
as that of the Cu2 +chelate. Compared with other divalent
cations, it is strong (Me Bride 1989). In this work the
bonding strengths of various divalent cations were
compared with the bonding strength for Ca2+ with three
different compounds: humic acid, acetic acid and citric acid.
For most of the cation species tested citricacidformedby far
IJTSRD33515
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD33515 | Volume – 4 | Issue – 6 | September-October 2020 Page 902
the strongest bonds because of its capability of chelating the
cation. Bonding strengths formed by the cations and
carboxylate group of acetic acid and humic acid were much
weaker. Of all the cation species tested, however, the bonds
formed by Cu2 + were by far the strongest.
The equilibrium concentration of Cu" maintained by
sparingly soluble Cu2 + salts suchascarbonatesandoxidesis
higher than the normal levels of Cu2 + in the soil solution.
The presence of carbonates or oxides in the soil therefore
plays no part in restricting Cu2+ solubility. The Cu2 +
concentration in the soil solution is governed by Cu
adsorption to organic and inorganic soil particles. For this
reason Cu is very immobile in soils and practically not
leached in to deeper soil layers. Copper added to the soil asa
result of the use of Cu containing sprays or fertilizers is thus
largely restricted to the upper soil horizons. (Delas, 1963)
The Cu concentration of many soils therefore decreases
down the profile. Copper displacement from soils can be
brought about either by strong acids or the use of organic
compounds which form Cu complexes. The significance of
these complexing reagents can be appreciated by the fact
that KCN is capable of extracting more than 50% of the total
soil Cu whereas non-complexing reagents extract only very
small quantities. (Beringer, 1963)
Copper can be released intotheenvironmentbybothnatural
sources and human activities. Examples of natural sources
are wind-blown dust, decaying vegetation, forest fires and
sea spray. A few examples of human activities that
contribute to copperrelease havealreadybeennamed.Other
examples are mining, metal production, wood production
and phosphate fertilizer production. Because copper is
released both naturally and through humanactivityitisvery
widespread in the environment. Copper is often found near
mines, industrial settings, landfills and waste disposals.
Most copper compounds will settle and be bound to either
water sediment or soil particles. Soluble copper compounds
form the largest threat to human health. Usually water-
soluble copper compounds occur in the environment after
release through application in agriculture. When copper
ends up in soil it strongly attaches to organic matter and
minerals. As a result it does not travel very far after release
and it hardly ever enters groundwater. In surface water
copper can travel great distances, either suspended on
sludge particles or as free ions. Copper does not break down
in the surroundings and because of that it can accumulate in
plants and animals when it is found in soils. On copper-rich
soils only a limited number of plants have a chance of
endurance. That is why there is not much plant diversity
near copper-disposing factories. Due to the effects upon
plants copper is a serious threat to the productions of
farmlands. Copper canseriouslyinfluencetheproceedingsof
certain farmlands, depending upon the acidityofthesoil and
the presence of organic matter. Despite of this, copper-
containing manures are still applied.
MICROBS AND COPPER
Bacterial interaction with surfaces is everywhere in nature.
For centuries, human civilizations haveused metalliccopper
in medicine, due to its antibacterial properties,until thestart
of commercially available antibiotics in 1932. Bacterial
interaction is bio corrosion, which is a type of metal
corrosion that occurs when microorganisms present in
different environments alter metal−solution interface
condition causing a strong interaction that considerably
accelerates mechanical failure of metals in a wide range of
environments.
UTILIZE OF COPPER
In a natural state, copper is hardly ever found pure (Badiye
et al, 2013). The metal is highly conductiveofbothelectricity
and heat, and many of its uses take advantage of this quality.
Copper can be found in many electronics and in wiring. It is
also used to make cooking pots. This metal is also relatively
corrosion resistant. For this reason, it's often mixed with
other metals to form alloys such as bronze and brass. The
metal is closely related with silver and gold, with many
properties being sharedamongthesemetals.Modernlife has
a number of applications for copper, ranging from coins to
pigments, and demand for the metal remainshigh,especially
in industrialized nations. Many regulars interact with it in
various forms on a daily basis. (Badiye et al., 2013) Most
copper is used for electrical tools (60%); construction, such
as roofing and plumbing (20%); industrial machinery, such
as heat exchangers (15%) and alloys (5%). The main long
established copper alloys are bronze, brass (a copper-zinc
alloy), copper-tin-zinc, which was strong enough to make
guns and cannons, and was known as gun metal, copper and
nickel, known as cupronickel, whichwasthepreferredmetal
for low-denomination coins. (Mengel et al., 2018) Copper is
ideal for electrical wiring because it is easily worked, can be
drawn into fine wire and has a high electrical conductivity.
Table 1 shows the Alloys of Cu. (Mengel et al., 2018)
Table: 1 Different alloys mixing with copper
Copper + Zinc = Brass
Copper + Tin = Bronze
Copper + Nickel = Cupronickel
Copper + Aluminium = Aluminium Bronze
Copper + Arsenic = Arsenical Copper
Copper + Tungsten = Copper Tungsten
Copper + Tin + Zinc = Gunmetal
ROLE OF Cu IN PLANT BIOLOGY
The rise of photosynthetic organisms on Earth has driven a
progressive addition of oxygen in the environment. This
oxidative atmosphere led to a decreased solubilityofiron by
the formation of iron oxides and to the progressive
liberation of soluble Cu (II) from insoluble Cu sulphide salts.
(Burkhead et al., 2009) Iron in biological moleculeshasbeen
gradually substituted by Cu which is able to perform similar
functions. This explains why many Cu-proteins have
purposeful counterparts that use Fe as cofactor and why
growth on a substrate with a toxic Cu level is commonly
linked to a decreased Fe-content in roots and leaves.
(Burkhead et al., 2009) Plant phenotypes associatedwith Cu
toxicity split similarities with those associated to Fe-
deficiency, such as the incidence of leaf chlorosis, decreased
leaf chlorophyll substance and enhanced oxidative tension.
(Pätsikkä et al., 2002) In contrast, copper deficient plants
develop chlorotic symptoms that show first at the tip of the
young leaves earlier forming necrotic lesions. Plants grown
under Cu deficiency also explain impairment in the
photosynthetic transport chain and a reduction in non-
photochemical quenching, which is consistent with a lack of
plastocyanin (PC) function. (Abdel-Ghany; Pilon, 2008)
In living organisms, the main functions of Cu are the
transport of electrons in mitochondria and chloroplasts(the
most abundant Cu protein is plastocyanin,a photosynthesis-
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD33515 | Volume – 4 | Issue – 6 | September-October 2020 Page 903
related protein involved in the transfer of electrons from
cytochrome f to P700+), they have power over of the cellular
redox state (a major Cu-binding protein is the Cu/Zn
superoxide dismutase) but also the remodelling of the cell
wall (Cohu; Pilon, 2010).
TOXICITY OF COPPER
As Cu deficiency occurs primarily on humus moneyed soils
which bind Cu2+ strongly, it may be made-up that certain
defined organic forms are more readily able to render Cu
occupied. (Mengel et al., 2018) Copper is notpoisonousin its
metallic state but some of its salts are poisonous, especially
the most common salts of copper are the Sulphate or the
blue vitriol (Nila; Tutia) and the sub-acetate or Verdigris
(Zangal). Copper Sulphate is a crystalline salt with blue
colour and metallic taste in a small dose of 0.5 g it acts as an
emetic but in large doses, as an irritant poison produces
gastric and intestinal irritation. Copper sub-acetate is a blue
green salt formed by the action of vegetable acids on copper
cooking vessels which are not properlylinedand whichhave
been used for cooking and storage for a long time. Copper
compounds of Arsenic include Scheele’s green (Copper
Arsenite), Paris green or emerald green (Copper Aceto-
arsenite) etc and go by the name “Hirwa” in the local
language .Copper is a powerful inhibitor of enzymes.
Poisoning effect of copper will commence within 15-30
minutes. (Badiye et al, 2013) Copper toxicity affected the
growth of Alyssum montanum (Ouzounidou 1994)andCdof
cucumber (Moreno-Caselles et al. 2000) and Brassica
juncea. (Singh and Tewari 2003) Copper and Cd in
combination have affected adversely the germination,
plantlet length and number of lateral roots in Solanum
melongena. (Neelima and Reddy 2002)
COPPER TOXICITY IN PLANT
Although soil hardly ever produces excessive amount of
copper on its own, copper toxicity can occur from the
repeated use of fungicides that contain copper. Copper
toxicity plants appear diminutive, are usually bluish in
colour, and eventually turn yellow or brown. Toxic copper
levels reduce seed germination,plantvigour,andironintake.
Neutralizing copper soil toxicity is extremely difficult once
the problem occurs. Copper haslowsolubility,whichenables
it to persist in the soil for years.
Figure: 1 Copper deficient plant
Cu METABOLISM
Copper is taken up by plants mainly through the rootsystem
and partly in minor amounts through the shoots and leaves.
(Mattioni et al., 1997) Copper (Cu) is considered as a
micronutrient for plants (Thomas et al. 1998) and plays
important role in CO2 assimilation and ATP synthesis. Cu is
also an essential component of various proteins like
plastocyanin of photosynthetic system and cytochrome
oxidase of respiratory electron transport chain.
(Demirevska-kepova et al., 2004) Under physiological
conditions, the conversion metal Cu is found in the two
common forms, the reduced Cu (I) state and the oxidized Cu
(II) state. Depending on this state, Cu can bind different
substrates. In its reduced form Cu(I) preferentially binds
sulphur-containing compounds having a thiol or a thioether
group, whereas the oxidized form Cu(II) coordinates mainly
with oxygen or imidazole nitrogen groups. (Cohu; Pilon,
2010) This dual chemistry of Cu allows it tocooperatewitha
large range of molecules, in fastidious proteins, to drive
biochemical reaction or stabilize structural features. (Festa;
Thiele, 2011) However, being redox active free Cu can
directly lead to the generation of reactive oxygen species
(ROS) through Fenton chemistry thereby cause damage to
proteins, DNA and other bio molecules. (Hänsch; Mendel,
2009)
COPPER DEFICIENCY IN PLANT
Copper is immobile, meaning its deficiency symptoms occur
in the newer leaves. Symptoms vary depending on the
crop. Typically, the symptoms start as cupping and a slight
chlorosis of either the whole leaf or between the veins of the
new leaves. Within the chlorotic areas of the leaf, small
necrotic spots may form, especially on the leaf margins. As
the symptoms progress, the newest leaves are smaller in
size, lose their sheen and in some cases the leaves may wilt.
The apical meristems may become necrotic and die,
inhibiting the growth of lateral branches. Plants typically
have a compact appearance as the stem length between the
leaves shortens. Flower colour is often lighter than normal.
(McElroy et al., 2017) Excess potassium, phosphorus or
other micronutrients can indirectly cause copper
deficiency. Also if the pH of the growing medium is high, this
can induce a copper deficiency as it is less available for plant
uptake. (McElroy et al., 2017)
FUTURE ASPECT
Applications of nonmaterial in agricultural production
and crop Protection
Implication of copper for Phytoremediation
Use of Copper to made up nanoparticles to the
terrestrial plants
Use of copper as a nanoparticle for controlling the
insect, pests and and pathogenic Microbes
BIBLIOGRAPHY
[1] https://doi.org/10.1007/978-94-010-1009-2_16
[2] https://doi.org/10.1007/978-981-10-9044-8
[3] https://doi.org/10.1016/j.jclepro.2018.04.116
[4] https://doi.org/10.1080/08927014.2017.1384468
[5] https://doi.org/10.3390/min8020032
[6] https://www.gardeningknowhow.com/garden-how-
to/soil-fertilizers/copper-for-the-garden.htm
[7] https://www.jstor.org/stable/41390000
[8] www.copperalliance.eu
[9] www.isca.in
[10] www.lenntech.com
[11] www.pthorticulture.com

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Role of Copper in Environment as a Potential and Challenges

  • 1. International Journal of Trend in Scientific Research and Development (IJTSRD) Volume 4 Issue 6, September-October 2020 Available Online: www.ijtsrd.com e-ISSN: 2456 – 6470 @ IJTSRD | Unique Paper ID – IJTSRD33515 | Volume – 4 | Issue – 6 | September-October 2020 Page 901 Role of Copper in Environment as a Potential and Challenges Dharmpal Meet A1, Rathod Zalak R2 1Department of Biotechnology, Kadi Sarva Vishwavidyalaya, Gandhinagar, Gujarat, India 2Department of Microbiology and Biotechnology, University School of Sciences, Gujarat University, Ahmedabad, Gujarat, India ABSTRACT Copper is a normally mixing component. Present in the world's shell, in seas, lakes and waterways, wellsprings of copper extend from minute follow sums to rich mine stores. Copper is a fundamental component, implying that all plants, fish and creatures need copper to work appropriately. All around the market for copper is one of the biggest of all metals following iron and aluminium. Copper can be delivered into the earth by both characteristic sources and human exercises. Present day life has various applications for copper, extending from coins to colours, and interest for the metal stays high, particularly in industrialized countries. KEYWORDS: Copper; Microbes; Iron; Aluminium; Metal How to cite this paper: Dharmpal Meet A | Rathod Zalak R "Role of Copper in Environment as a Potential and Challenges" Published in International Journal of Trend in Scientific Research and Development(ijtsrd), ISSN: 2456-6470, Volume-4 | Issue-6, October 2020, pp.901-903, URL: www.ijtsrd.com/papers/ijtsrd33515.pdf Copyright © 2020 by author(s) and International Journal ofTrendinScientific Research and Development Journal. This is an Open Access article distributed under the terms of the Creative CommonsAttribution License (CC BY 4.0) (http://creativecommons.org/licenses/by/4.0) INTRODUCTION Copper is a naturally stirring element. Present in the earth’s shell, in oceans, lakes and rivers, sources of copper range from minute trace amounts to rich mine deposits. Copper is an essential element, meaning that all plants, fish and animals need copper to function properly. (copperalliance.eu) Copper contamination is one of the major environmental hazards in contaminated areas (Chaney et al., 1997). Normal concentration of copper in plant tissues is approximately 5-25 mg/kg. Copper toxicity due to many aspects of its behaviour inhibits iron metabolism and the activities of many enzymes (Hou et al., 2007). Universally the market for copperisoneofthelargest of all metals following iron and aluminium. The size of the largely market for developed copper is over U$149 billion every year, Copper has been a material component in the growth of human civilizationsforthousandsofyears.India is one of the top 20 major producers ofcopperuniversally.Asa result, instability in prices of the metal on the LME has an important bearing on Indian copper trading. Over 30% of India‘s copper demand comes from the telecom sector and 26% from the electrical sector. In addition, the building and construction, engineering, transportandconsumerdurables sectors are major consumers of copper in India. (Kabwe; Yiming, 2015) Environmental form of copper Copper occurs in the soil almost excl suavely in divalent form. The largest fraction of Cu is usually present in the precious stone latticesofprimaryandsecondaryminerals.In addition a high fraction of Cu is bound by the soil organic matter. The Cu ion is adored to inorganic and organic negatively charged groups and is dissolved in the soil way out as Cu2 + and organic Cu complexes. Copper is specifically adsorbed to carbonates, soil organic matter, phyllo silicates, and hydrous oxides of AI, Fe, and Mn. (Reed; Martens, 1996) The focus of Cu2 + in the soil solution decreases sharplywith an increasing pH where as the concentration of organic Cu complex in the soil explanation is less dependent on soil pH. Higher pH may even promote the termination of organic Cu complexes. The divalent Cu ion has a strong affinity to soil organic matter compared with other divalent cations as is shown by the following sequence (Schnitzer, 1965; Skinner, 1967): Cu > Ni > Pb > Co > Ca > Zn > Mn > Mg Copper may be bound in chelated form to organic matter which means that it is held by covalent and coordinative bonds. It is coordinatively bound to 0, N, and S atoms following the preference S > N > O. Since N is present in soil organic material in much higher concentrations than S, N atomstake part in the major role in chelating Cu2+ inquantitativeterms. Recent findings indicate that a large proportion of Cu2+ is also bound covalently to carboxylic groupsasoccurinhumic and fulvic acids in soil organic matter and as shown below. This is covalent mono dentate binding of Cu2 + to the carboxylic group R-COO- + Cu2+= R-COO Cu+ is not as strong as that of the Cu2 +chelate. Compared with other divalent cations, it is strong (Me Bride 1989). In this work the bonding strengths of various divalent cations were compared with the bonding strength for Ca2+ with three different compounds: humic acid, acetic acid and citric acid. For most of the cation species tested citricacidformedby far IJTSRD33515
  • 2. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD33515 | Volume – 4 | Issue – 6 | September-October 2020 Page 902 the strongest bonds because of its capability of chelating the cation. Bonding strengths formed by the cations and carboxylate group of acetic acid and humic acid were much weaker. Of all the cation species tested, however, the bonds formed by Cu2 + were by far the strongest. The equilibrium concentration of Cu" maintained by sparingly soluble Cu2 + salts suchascarbonatesandoxidesis higher than the normal levels of Cu2 + in the soil solution. The presence of carbonates or oxides in the soil therefore plays no part in restricting Cu2+ solubility. The Cu2 + concentration in the soil solution is governed by Cu adsorption to organic and inorganic soil particles. For this reason Cu is very immobile in soils and practically not leached in to deeper soil layers. Copper added to the soil asa result of the use of Cu containing sprays or fertilizers is thus largely restricted to the upper soil horizons. (Delas, 1963) The Cu concentration of many soils therefore decreases down the profile. Copper displacement from soils can be brought about either by strong acids or the use of organic compounds which form Cu complexes. The significance of these complexing reagents can be appreciated by the fact that KCN is capable of extracting more than 50% of the total soil Cu whereas non-complexing reagents extract only very small quantities. (Beringer, 1963) Copper can be released intotheenvironmentbybothnatural sources and human activities. Examples of natural sources are wind-blown dust, decaying vegetation, forest fires and sea spray. A few examples of human activities that contribute to copperrelease havealreadybeennamed.Other examples are mining, metal production, wood production and phosphate fertilizer production. Because copper is released both naturally and through humanactivityitisvery widespread in the environment. Copper is often found near mines, industrial settings, landfills and waste disposals. Most copper compounds will settle and be bound to either water sediment or soil particles. Soluble copper compounds form the largest threat to human health. Usually water- soluble copper compounds occur in the environment after release through application in agriculture. When copper ends up in soil it strongly attaches to organic matter and minerals. As a result it does not travel very far after release and it hardly ever enters groundwater. In surface water copper can travel great distances, either suspended on sludge particles or as free ions. Copper does not break down in the surroundings and because of that it can accumulate in plants and animals when it is found in soils. On copper-rich soils only a limited number of plants have a chance of endurance. That is why there is not much plant diversity near copper-disposing factories. Due to the effects upon plants copper is a serious threat to the productions of farmlands. Copper canseriouslyinfluencetheproceedingsof certain farmlands, depending upon the acidityofthesoil and the presence of organic matter. Despite of this, copper- containing manures are still applied. MICROBS AND COPPER Bacterial interaction with surfaces is everywhere in nature. For centuries, human civilizations haveused metalliccopper in medicine, due to its antibacterial properties,until thestart of commercially available antibiotics in 1932. Bacterial interaction is bio corrosion, which is a type of metal corrosion that occurs when microorganisms present in different environments alter metal−solution interface condition causing a strong interaction that considerably accelerates mechanical failure of metals in a wide range of environments. UTILIZE OF COPPER In a natural state, copper is hardly ever found pure (Badiye et al, 2013). The metal is highly conductiveofbothelectricity and heat, and many of its uses take advantage of this quality. Copper can be found in many electronics and in wiring. It is also used to make cooking pots. This metal is also relatively corrosion resistant. For this reason, it's often mixed with other metals to form alloys such as bronze and brass. The metal is closely related with silver and gold, with many properties being sharedamongthesemetals.Modernlife has a number of applications for copper, ranging from coins to pigments, and demand for the metal remainshigh,especially in industrialized nations. Many regulars interact with it in various forms on a daily basis. (Badiye et al., 2013) Most copper is used for electrical tools (60%); construction, such as roofing and plumbing (20%); industrial machinery, such as heat exchangers (15%) and alloys (5%). The main long established copper alloys are bronze, brass (a copper-zinc alloy), copper-tin-zinc, which was strong enough to make guns and cannons, and was known as gun metal, copper and nickel, known as cupronickel, whichwasthepreferredmetal for low-denomination coins. (Mengel et al., 2018) Copper is ideal for electrical wiring because it is easily worked, can be drawn into fine wire and has a high electrical conductivity. Table 1 shows the Alloys of Cu. (Mengel et al., 2018) Table: 1 Different alloys mixing with copper Copper + Zinc = Brass Copper + Tin = Bronze Copper + Nickel = Cupronickel Copper + Aluminium = Aluminium Bronze Copper + Arsenic = Arsenical Copper Copper + Tungsten = Copper Tungsten Copper + Tin + Zinc = Gunmetal ROLE OF Cu IN PLANT BIOLOGY The rise of photosynthetic organisms on Earth has driven a progressive addition of oxygen in the environment. This oxidative atmosphere led to a decreased solubilityofiron by the formation of iron oxides and to the progressive liberation of soluble Cu (II) from insoluble Cu sulphide salts. (Burkhead et al., 2009) Iron in biological moleculeshasbeen gradually substituted by Cu which is able to perform similar functions. This explains why many Cu-proteins have purposeful counterparts that use Fe as cofactor and why growth on a substrate with a toxic Cu level is commonly linked to a decreased Fe-content in roots and leaves. (Burkhead et al., 2009) Plant phenotypes associatedwith Cu toxicity split similarities with those associated to Fe- deficiency, such as the incidence of leaf chlorosis, decreased leaf chlorophyll substance and enhanced oxidative tension. (Pätsikkä et al., 2002) In contrast, copper deficient plants develop chlorotic symptoms that show first at the tip of the young leaves earlier forming necrotic lesions. Plants grown under Cu deficiency also explain impairment in the photosynthetic transport chain and a reduction in non- photochemical quenching, which is consistent with a lack of plastocyanin (PC) function. (Abdel-Ghany; Pilon, 2008) In living organisms, the main functions of Cu are the transport of electrons in mitochondria and chloroplasts(the most abundant Cu protein is plastocyanin,a photosynthesis-
  • 3. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD33515 | Volume – 4 | Issue – 6 | September-October 2020 Page 903 related protein involved in the transfer of electrons from cytochrome f to P700+), they have power over of the cellular redox state (a major Cu-binding protein is the Cu/Zn superoxide dismutase) but also the remodelling of the cell wall (Cohu; Pilon, 2010). TOXICITY OF COPPER As Cu deficiency occurs primarily on humus moneyed soils which bind Cu2+ strongly, it may be made-up that certain defined organic forms are more readily able to render Cu occupied. (Mengel et al., 2018) Copper is notpoisonousin its metallic state but some of its salts are poisonous, especially the most common salts of copper are the Sulphate or the blue vitriol (Nila; Tutia) and the sub-acetate or Verdigris (Zangal). Copper Sulphate is a crystalline salt with blue colour and metallic taste in a small dose of 0.5 g it acts as an emetic but in large doses, as an irritant poison produces gastric and intestinal irritation. Copper sub-acetate is a blue green salt formed by the action of vegetable acids on copper cooking vessels which are not properlylinedand whichhave been used for cooking and storage for a long time. Copper compounds of Arsenic include Scheele’s green (Copper Arsenite), Paris green or emerald green (Copper Aceto- arsenite) etc and go by the name “Hirwa” in the local language .Copper is a powerful inhibitor of enzymes. Poisoning effect of copper will commence within 15-30 minutes. (Badiye et al, 2013) Copper toxicity affected the growth of Alyssum montanum (Ouzounidou 1994)andCdof cucumber (Moreno-Caselles et al. 2000) and Brassica juncea. (Singh and Tewari 2003) Copper and Cd in combination have affected adversely the germination, plantlet length and number of lateral roots in Solanum melongena. (Neelima and Reddy 2002) COPPER TOXICITY IN PLANT Although soil hardly ever produces excessive amount of copper on its own, copper toxicity can occur from the repeated use of fungicides that contain copper. Copper toxicity plants appear diminutive, are usually bluish in colour, and eventually turn yellow or brown. Toxic copper levels reduce seed germination,plantvigour,andironintake. Neutralizing copper soil toxicity is extremely difficult once the problem occurs. Copper haslowsolubility,whichenables it to persist in the soil for years. Figure: 1 Copper deficient plant Cu METABOLISM Copper is taken up by plants mainly through the rootsystem and partly in minor amounts through the shoots and leaves. (Mattioni et al., 1997) Copper (Cu) is considered as a micronutrient for plants (Thomas et al. 1998) and plays important role in CO2 assimilation and ATP synthesis. Cu is also an essential component of various proteins like plastocyanin of photosynthetic system and cytochrome oxidase of respiratory electron transport chain. (Demirevska-kepova et al., 2004) Under physiological conditions, the conversion metal Cu is found in the two common forms, the reduced Cu (I) state and the oxidized Cu (II) state. Depending on this state, Cu can bind different substrates. In its reduced form Cu(I) preferentially binds sulphur-containing compounds having a thiol or a thioether group, whereas the oxidized form Cu(II) coordinates mainly with oxygen or imidazole nitrogen groups. (Cohu; Pilon, 2010) This dual chemistry of Cu allows it tocooperatewitha large range of molecules, in fastidious proteins, to drive biochemical reaction or stabilize structural features. (Festa; Thiele, 2011) However, being redox active free Cu can directly lead to the generation of reactive oxygen species (ROS) through Fenton chemistry thereby cause damage to proteins, DNA and other bio molecules. (Hänsch; Mendel, 2009) COPPER DEFICIENCY IN PLANT Copper is immobile, meaning its deficiency symptoms occur in the newer leaves. Symptoms vary depending on the crop. Typically, the symptoms start as cupping and a slight chlorosis of either the whole leaf or between the veins of the new leaves. Within the chlorotic areas of the leaf, small necrotic spots may form, especially on the leaf margins. As the symptoms progress, the newest leaves are smaller in size, lose their sheen and in some cases the leaves may wilt. The apical meristems may become necrotic and die, inhibiting the growth of lateral branches. Plants typically have a compact appearance as the stem length between the leaves shortens. Flower colour is often lighter than normal. (McElroy et al., 2017) Excess potassium, phosphorus or other micronutrients can indirectly cause copper deficiency. Also if the pH of the growing medium is high, this can induce a copper deficiency as it is less available for plant uptake. (McElroy et al., 2017) FUTURE ASPECT Applications of nonmaterial in agricultural production and crop Protection Implication of copper for Phytoremediation Use of Copper to made up nanoparticles to the terrestrial plants Use of copper as a nanoparticle for controlling the insect, pests and and pathogenic Microbes BIBLIOGRAPHY [1] https://doi.org/10.1007/978-94-010-1009-2_16 [2] https://doi.org/10.1007/978-981-10-9044-8 [3] https://doi.org/10.1016/j.jclepro.2018.04.116 [4] https://doi.org/10.1080/08927014.2017.1384468 [5] https://doi.org/10.3390/min8020032 [6] https://www.gardeningknowhow.com/garden-how- to/soil-fertilizers/copper-for-the-garden.htm [7] https://www.jstor.org/stable/41390000 [8] www.copperalliance.eu [9] www.isca.in [10] www.lenntech.com [11] www.pthorticulture.com