Muhammad, Zafar Iqbql 1, Maria,
Khan Siddiqui 1, Mohammad, Athar*2, 3 Muhammad,
Shafiq 1, Zia-Ur-Rehman Farooqi1 Muhammad,
Kabir 1
1Department of
Botany, University of Karachi, Karachi-75270, Pakistan
2 Department of Food Science and Technology, University of Karachi,
Karachi-75270, Pakistan
3 California Department of Food and Agriculture, 3288 Meadowview Road,
Sacramento, CA 95832,
USA.
(*Corresponding
Author’s e-mail: atariq@cdfa.ca.gov)
KEYWORDS: Mercury, mungbean, seed germination,
toxicity, plant growth, biomass production.
Abstract
Among the toxic elements release in the
environment, mercury is considered highly toxic to the growth of plants. The present studies report the effects of
different concentrations (1, 3, 5 and 7 mM) of mercury on seed germination and
seedling growth performance of mungbea (Vigna
radiata) as compared to control.
Mercury treatment in the form of mercuric chloride at 1 mM did not show
significant reduction in seed germination of V. radiata as compared to control.
Increase in concentration of mercury to 3 mM produced significant
(p<0.05) reduction in seed germination.
Mercury treatment at 7 mM-produced significant (p<0.05) reduction in
seedling and root length of the plants.
The increase in concentration of mercury treatment at 7 mM was found
sufficient to cause significant reductions in seedling dry weight of as
compared to control. Mercury treatment
at all concentrations decreased seed germination, shoot, and root length and
seedling dry weight. Increase in mercury
concentration upto 7 mM showed highest percentage of decrease in seed
germination (42%), seedling length (70%), root length (66%) and seedling dry
weight (47%) of mungbean as relation
to control. V. radiata were more sensitive to mercury stress in seedling growth
and root elongation than seed germination.
The seedlings of V. radiata
showed greater tolerance to mercury at 1 mM (85.83 %) and lowest at 7 mM
(34.13%). These results show that there
is a negative effect towards germination and growth of mungbean by mercury
treatment. Minimum use of the mercury
containing compounds in fungicide, pesticide and nematicide is
recommended. Special care should be
taken to monitor the toxic pollutants available in the immediate environment. The accumulation of such types of toxic
pollutants in larger concentrations by crop can produce harmful effects to
crops and ecosystem as well. © JASEM.
Introduction
Rapid increase in the industrial and anthropogenic activities and discharge of untreated chemicals in the environment are responsible for spreading of different types of chemical compounds in the air, soil and water, affecting the environment and growth of plants. Among the toxic elements release in the environment, mercury is considered highly toxic to the growth of plants (Iqbal et al., 2014). During the past couple of decades the concentrations of heavy metals in the environment of city have appeared at dangerous level. Mercury also used for eliminating various pests causes harmful effects on agricultural plants (Simon, 2014). They produce toxic effects on the leaves where crucial functions such as photosynthesis and transpiration are carried out, cause morphological, anatomical and physiological changes, inhibit pollen germination and pollen tube formation and thus affect fruit production (Simon, 2014; Tort et al., 2005). Seed health plays an important role for successful cultivation and yield
*Corresponding Author’s e-mail: atariq@cdfa.ca.gov
exploitation of a crop species (Rajput et al., 2005). Attention has been
given, in developed countries, about the effects of metal toxicities on
germination and growth of plants.
Mercury (5 µM HgCl2), a general blocker of
aquaporins in various organisms, reduced the speed of seed germination and induced a
true delay in maternal seed coat (testa) rupture and radicle emergence,
by 8-9 and 25-30 h, respectively (Willigen
et al., 2006). Mercury stress may result in decreased foliar
chlorophyll content and/or damage to internal leaf structure (Dunagan et al., 2007). Mercury contamination is widespread in
different ecological compartments such as atmosphere, soil and water. There is evidence showing bioaccumulation and
biomagnification of Hg in aquatic food chains, with higher concentrations
detected in carnivorous fish (Zhang and Wong, 2007). Mercury in the agricultural ecosystem is a
global concern because of its high potential toxicity (Iqbal et al., 2014;
Zheng et al., 2008).
Arsenic (As) and mercury (Hg) are among the most
dangerous heavy metals to humans and the environment because of their toxicity
towards all living organisms and their related accumulation capability (Bini
and Bech, 2014; Comino et al., 2009).
Mercury
is released to the atmosphere from natural and anthropogenic sources. Due to its persistence in the atmosphere,
mercury is subject to long range transport and is thus a pollutant of global
concern. Mercury emitted to the
atmosphere enters terrestrial and aquatic ecosystems which act as sinks but
also as sources of previously emitted and deposited mercury when the
accumulated mercury is emitted back to the atmosphere (Baya and Van Heyst,
2010). Environmental contamination
caused by mercury is a serious problem worldwide. Coal combustion, mercury and gold mining
activities and industrial activities have led to an increase in the mercury
concentration in soil (Wang et al.,
2012).
Mercury is a global environmental pollutant that is present
in soil, water, air and biota. The
effect of increasing rates of mercury (10, 25, 50 and 75 mg/kg) treatments in Catharanthus roseus was observed on
plant viability. The increase in
concentration of heavy metal decreases plant growth and leads to its death
(Iqbal et al., 2014; Kumar et al.,
2011). The effect of mercuric acetate on
seedling growth, total chlorophyll, chlorophyll a and b, reducing, nonreducing
and total sugar content, protein content and lipid content was studied in
peanut plants (Arachis hypogaea) at
0.0001 mM and 0.001 mM concentrations.
Reduction in length was more in roots than in shoots. Chlorophyll-a, chlorophyll-b and total
chlorophyll contents decreased significantly under mercuric acetate treatment
(Bhanumathi et al., 2005).
In vivo cytogenetic assay in Allium
cepa root tip cells has been carried out to detect the modifying effect of Ocimum sanctum aqueous leaf extract
against chromium and mercury induced genotoxicity. It was observed that the root post-treated
with the leaf extract showed highly significant (p<0.001) recovery in
mitotic index (MI) and chromosomal aberrations (CA) when compared to
pre-treated (Cr/Hg) samples and the lower doses of the leaf extract were found
to be more effective than bigger doses (Babu and Maheshwari, 2006). Seeds of cabbage (Brassica rapa), cole (B.
napus), head cabbage (B. oleracea),
and spinach (Spinacia oleracea) were found significantly
inhibited when treated with HgCl2 concentration upto 8
mM. B.
oleracea was the most sensitive species to mercury among the four test
species, B. campestris was the most
resist species to mercury pollution. These
four vegetables were more sensitive to mercury stress in coleoptile growth and
root elongation than seed germination (Ling et al., 2010). Mercury
contamination of the environment is of worldwide concern because of its global
presence and its potent neurotoxicity.
Mining, smelting and the electronics industry are the main sources of
mercury pollution (Deng et al.,
2011).
The genus Vigna contains several species that are important in the world
agriculture. Cowpeas (V. unguiculata),
mungbeans (V. radiata) and urd beans
(V. mungo) provide a significant
portion of the dietary protein in many societies. All of the cultivated Vigna species can be grown over a wide range of environmental
conditions. The mungbeans are widely
grown in southern Asian countries.
In Pakistan substantial
quantities of agricultural chemicals are used annually to enhance yield (Nuzhat
et al., 2005). Mercuric chloride (HgCl2), the
main representative of mercury compounds, is the target of numerous
investigations, not only because of its intrinsic toxicity but also because it
accounts for the toxicity of elemental mercury since the latter is converted to
Hg+2 by oxidation (Sobral-Souza et al., 2014). The ever increase
in mercury concentration over the wide areas of Karachi and rural areas raises
serious questions as to its effects on the growth and vigor of plants. A decline in the agriculture areas play an
important role which can lead to certain restriction in the availability of crop
for human beings. The data on the effects
of mercury on mungbean crop is presently seems scanty. The increase in concentration of metals like
mercury can produce toxic effects on plants growth. The response of plant growth to toxic effects
of heavy metals has become the subject of great interest in recent years
because of their nature of high toxicity to plants. Attention has been given in developed
countries, about the effects of metal toxicities on plants growth. Therefore, a study was carried out to
determine the effect of mercury on seed germination and seedling growth of an
important crop mungbean (V. radiata).
MATERIALS AND METHODS
Certified and healthy seeds of
mungbean {Vigna radiata (L.) Wilczek
(Fabaceae)} were purchased from a local seed company. The seeds were surface sterilized with dilute
solution of sodium hypochlorite for one minute to avoid any fungal
contamination. The seeds were washed
with distilled water and transferred in Petri dishes (90 mm diameter) on filter
paper at room temperature. There were
three replicates. Initially, 5 ml
solution of mercuric chloride in different ranges 1, 3, 5 and 7 mM were
applied. All solutions were changed
daily. The control treatment consisted
of just the distilled water. After seven
days, seed germination percentage, root and seedling length were noted for V. radiata. The seedling dry weight was determined by
drying the plant materials in an oven at 800C for 24 hours. The data obtained were statistically analyzed
by Analysis of variance and Duncan's Multiple Range Test. A tolerance index was determined by the
following formula as described by Iqbal and Rahmati (1992).
Mean root length in metal
solution/Mean root length in distilled water X 100.
RESULTS AND DISCUSSION
The seed germination and seedling growth performance of V. radiata were tested in different
concentrations (1, 3, 5 and 7 mM) of mercury as compared to control
(Fig.1). Mercury treatment in the form
of mercuric chloride at 1 mM did not produce any significant (p<0.05)
reduction in seed germination of V.
radiata as compared to control.
Increase in concentration of mercury at 3 mM produced significant
reduction in seed germination. Root
growth is an important growth variable and found affected by mercury
treatment. The treatment of mercury at 7
mM produced significant (p<0.05) reduction in root length of V. radiata. The results also showed that mercury
treatment in the substrate from 1 to 5 mM did not produce any significant
effect on seedling dry weight of V.
radiata as compared to control.
However, increase in concentration of mercury treatment at 7 mM was
found sufficient to cause significant reductions in seedling dry weight of V. radiata as compared with control.
The elements have specific function all of them are
known to be involved in enzyme action.
However, plant under stress condition is most likely to be adversely
affected by high concentrations of trace elements. In present study, the effect of mercuric
chloride on seed germination, seedling growth, root length and seedling dry
weight of an important crop mungbean were recorded. Mercury induced oxidative stresses in Suaeda salsa and also mercury at a
concentration of 20 μg L−1 disturbed
protein biodegradation and energy metabolism in Suaeda salsa (Wu et al., 2011).
The seed germination of mungbean responded
differently to mercuric chloride treatment as compared to control. High percentage of decrease in seed
germination of mungbean provided evidence that the treatment of mercury in
excess may be inhibitory to plant growth and development. Inorganic mercury has been reported to
produce harmful effect at 5 µg L−1 in
culture medium for aquatic plants (Boeing, 2000). Germination rate and root elongation, as a
rapid phytotoxicity test methods, possesses several advantages such as
sensitivity, simplicity, low cost and suitability for unstable chemicals or
samples. Information on toxicity
required for the ecological risk assessment of toxic pollutants (Wang et al., 2001).
Plants experience oxidative stress upon exposure to heavy metals that leads to cellular damage (Kunjam et al., 2015; Nagati et al., 2015). In addition, plants accumulate metal ions that disturb cellular ionic homeostasis (Acharya and Sharma, 2014; Siddiqui et al., 2014). To minimize the detrimental effects of heavy metal exposure and their accumulation, plants have evolved detoxification mechanisms (Yadav, 2010). Metals are toxic to both plants and fungi, and elevated soil metal concentrations have been documented to change the structure of ectomycorrhizal communities and high concentrations of mercury (0-366 μg g-1 Hg) in soil decreased survival of Pinus rigida seedlings (Crane et al., 2012). The mercury uptake could produce serious damage to plants by impairment of the chlorophyll synthesis and reduction of photosynthesis as a result of substitution of Mg by Hg (Lavado et al., 2007). Metal toxicity is also an important factor governing germination and growth of plants. The permeability of metals can decreased the growth of plants. Reduction in seedling growth of V. radiata was observed when treated with different concentration of mercury. In field open top chambers (OTCs) and soil mercury enriched experiments when employed to study the influence of mercury concentrations in air and soil on the mercury accumulation in the organs of corn (Zea mays) and wheat (Triticum aestivum). The results showed that Hg concentrations in foliages were correlated significantly (p <0.05) with air Hg concentrations but insignificantly correlated with soil Hg concentrations. The author concluded that Hg in crop foliages was found mainly from air. Hg concentrations in roots were generally correlated with soil Hg concentrations (p < 0.05) but insignificantly correlated with air Hg concentrations, indicating that Hg in crop roots was mainly from soil (Niu et al., 2011).
Fig. 1.
Effects of different concentration of mercury treatment on seed germination
(%), seedling length (cm),
root length (cm) and seedling dry weight (g) for Vigna radiata as compared to control. Number followed by the same
letters in the same bar are not significantly different (p<0.05) according
to Duncan’s Multiple Range Test. Mercury
treatment at all concentration decreased seed germination, root length and
seedling dry weight of V. radiata
(Fig.2). Mercury treatment at 1 mM |
concentration
was less toxic for decrease in seed germination (16%), seedling length (21%),
root length (17%) and seedling dry weight (10%) as compared to control.
Mercury treatment at 5 mM concentration showed more decrease in seed
germination (37%), seedling length (27%), root length (21%) and seedling dry
weight (23%) of V. radiata. Mercury concentration of 7 mM decrease seed
germination (42%), seedling length (70%), root length (66%) and seedling dry
weight (47%) of V. radiata as
compared to control. |
Fig.
2. Percentage decrease in seed germination, seedling length, root length
and seedling dry weight of Vigna raddiata
using different concentration of
mercury.
The seedlings of V. radiata were also tested for (Fig. 3). V. radiata showed greater tolerance (85.83 percentage of tolerance to mercury. The results %) to mercury at 1 mM and lowest (34.33 %) at 7mM showed that V. radiata has greater tolerance to of mercury. V. radiata seedlings showed better mercury at 1 mM and lowest at 7mM of mercury percentage of tolerance 82.83 % to mercury at 3 mM.
Fig. 3. Percentage of tolerance in Vigna radiata using different concentration of mercury
The reduction in the seedling and root growth of V. radiata provides further evidence
that the mercury in excess may be inhibitory to plant growth and development. Mercury is one of the most toxic heavy metals
to living organisms and its conspicuous effect is the inhibition of root growth
(Wang et al., 2013). The root elongation tests have been used as
simple, rapid, reliable and reproducible techniques to evaluate the damage
caused by toxic compounds present in various composts (US-EPA, 1982). Many species including cabbage, lettuce,
carrot, cucumber, tomato and oats have been recommended for the phytotoxicity
test (F.D.A., 1982). The roots are
normally considered in relation to their ability to supply water and nutrients
to the plants. The root growth of V. radiata was found decreased by 66% at
7 mM mercury concentration. The results
of this investigation have shown that mercury treatment is more toxic for V. radiata for root development. Mercury content and distribution as well as
its effects on growth were investigated in 30 day-old tomato (Lycopersicon esculentum) seedlings (Chao
and Park, 2000). The results showed that
excess of mercury suppressed biomass production of both roots and shoots and
reduced chlorophyll content in tomato leaves.
The seedlings of alfalfa (Medicago
sativa) pretreated with 0.2 mM salycylic acid for 12 h and subsequently
exposed to 10 μM Hg2+ for 24 h displayed attenuated toxicity to the
root (Zhou et al., 2009). In another investigation, plants of Chilopsis linearis grown with 0, 50,
100, and 200 μM Hg [as Hg(CH3COO)2] and 0 and 50 μM Au
(as KAuCl4) in hydroponics showed that seedling grown with 50 μM Au
+ 50 μM Hg and 50 μM Au + 100 μM Hg had roots 25 and 55% shorter than control
roots, respectively (Rodríguez et al.,
2009).
Toxicants accumulate in the plant
when soluble forms are present in high quantities (Acharya and Sharma, 2014;
Nagati et al., 2015). The exact amount
of accumulation depends upon the solubility of the pollutants in the soil
(Kunjam et al., 2015; Siddiqui et al., 2014).
Under certain conditions, sufficient arsenic may be absorbed to injure
or kill sensitive plants, thus altering the community structure, or arsenic may
enter the leave sand thus is hazardous to any organisms feeding on them. The solubility of toxicants in the soil is greatly
affected by the soil acidity. Thus
greater amounts of metals such as zinc and aluminium become soluble and
absorbable in acid soils. This has
raised the question of whether sulphur, deposited in precipitation as sulphuric
acid, and later forming an acid reaction, could change the soil acidity to the
extent that certain elements such as aluminium, manganese, or zinc become toxic
(Treshow, 2010).
Conclusion: According to tolerance test it could be seen that
tolerance to mercury was higher at low concentration of mercury in the
seedlings of V. ratiata. These results showed that the reason of
tolerance against heavy metals might be a physiological association of the
tolerance mechanism to these metals. The
seedling growth of V. radiata showed
high percentage of tolerance to mercury at 1 mM concentration. 7 mM
concentration of mercury produced lowest percentage of tolerance in seedling of
mungbean.
The concentration of mercury like other metals in the
environment has been increased due to industrial and anthropogenic
activities. Such constant increase of
mercury in the environment is producing toxic effects on plant growth and can
severely limit the yield. The wealth of
information from the treatment of the mercury through seedling growth studies
would be helpful in controlling the mercury pollution problem. Reduction in seedling growth of V. radiata can be considered as an over
all indicator of plant vigor. The
findings may contribute to ecological fragility, the potential of crop in
coordinating in land management programmes.
They also stabilize the soil and in some cases improve it. The cultivation management of mungbean in
mercury-polluted area will help in reducing the burden of pollution to some
extent. Heavy reliance on mercury
containing fungicides can be discouraged to certain level and subsequently
continuous release of mercury into the immediate environment may endanger
freshwater life, drinking water reservoirs and use of crop for humans. Current research shows that mercury treatment
at different concentration has produced an important effect on seed germination
and seedling growth of V. radiata. Increase in the concentration of mercury in
the medium, brought up certain toxic changes in germination of V. radiata. These results show that there is a negative
effect towards germination and growth of mungbean by mercury treatment. Minimum use of the mercury containing
compounds in fungicide, pesticide and nematicide is recommended. Special care should be taken to monitor the
toxic pollutants available in the immediate environment. The accumulation of such types of toxic
pollutants in larger concentrations by crop can produce harmful effects to
crops and ecosystems. Special efforts
need to be made to identify sources of mercury toxicity and there is also a
need to carry out an ongoing effort to develop tolerance indices. Better sources of resistances to metal are
badly needed.
Acknowledgement
Sincere thanks are expressed to Dr. David Goorahoo, California State University, Fresno, CA, USA, Dr. Ozair Chaudhry, Albert Campbell Collegiate Institute (NS) Scarborough, Ontario, Canada; Prof. Dr. Seema Mahmood, University of Glasgow, Glasgow, Scotland for their critical comments and valuable suggestions on the manuscript.
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