Heavy metal pollution in soil and its mitigation aspect by Dr. Tarik Mitran
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Transcript of Heavy metal pollution in soil and its mitigation aspect by Dr. Tarik Mitran
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Heavy metal pollution in soil and its
possible mitigation aspect
Speaker: Dr.Tarik Mitran
Agricultural Chemistry and Soil Science
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What is a Heavy Metal?
The term heavy metal refers to any metallic chemical element that has a
relatively high density and is toxic or poisonous at low concentrations.
Examples of heavy metals include mercury (Hg), cadmium (Cd), arsenic
(As), chromium (Cr), thallium (Ti), and lead (Pb).
Heavy metals are those having densities five times greater than water,
and the light metals are those having lesser densities.
Humans consume metallic elements through both water and food.
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Source: Brady(1994)
It should be noted that the content of metals in tissue generally builds up from left to right, indicating the vulnerability of humans to heavy metal toxicity
Sources of heavy metals and their cycling in the soil-water-air organism ecosystem
Rocks in Earth’scrust
Air
Soil
Water
Plants
Birds
Domesticanimals
Fish
Humans
Industrial ProductsBurned fuelFertilizersPesticides
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Anthropogenic sources of heavy
metals in soil
Tannery
BatteryDistillery
Steel Fly ash
Electroplating Mining
Smelting
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Heavy metalHeavy metal
Transition metals
Ia IIaIIIa IVa Va VIa VIIa
Ib IIb
Lanthanides
Actinides
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Chemical Major uses and sources of soil contamination
Arsenic Pesticides, plant desiccants, animal feed additives, coal and petroleum, mine tailings and detergents
Cadmium Electroplating, pigments for plastics and paints, plastic stabilizers and batteries, fertilizers
Chromium Stainless steel, chrome–plated metals, pigments and refractory brick manufacture
Lead Combustion of oil, gasoline, and coal; iron and steel production
Mercury Pesticides, catalysts for synthetic polymers, metallurgy, thermometers
Nickel Combustion of coal, gasoline, and oil; alloy manufacture, electroplating, batteries
Source: Moore and Ramamoorthy (1984)
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Sources Annual Emission (T/year)
Natural SourcesWindblown dustForest firesVolcanogenic particlesVegetationSea salt spray
10012
5202001
Anthropogenic sources
Mining, non-ferrous metals
Primary non-ferrous metal Production
Cd
Cu
Pb
Zn
Secondary non-ferrous metal production
Iron and steel production
Industrial applications
Coal combustion
110
1600
200
2800
600
70
50
60
Table: Emission of Cadmium to the atmosphere
Source: Nriagu (1980) and Vogeli Lange (1989)
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ElementConcentration
range (mg/kg)
Regulatory limit
(mg/kg)
Lead 1-6900 600
Cadmium 0.1-345 100
Arsenic 0.1-102 20
Chromium 0.005-3950 100
Mercury 0.001-1800 270
Copper 0.03-1550 600
Zinc 0.15-5000 1500
Table: 2 Heavy metals prevailing in soils and their regulatory limits
Source: Salt et al (1994)
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Heavy Metals Limit in Soil
Source: Sherman, 2002
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Heavy Metals according to their Toxicity
Cd, As
Hg, Pb, Ni, F
B, Cu, Mn, Zn
Extremely poisonous
Moderately poisonous
Relatively less poisonous
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Behavior of Hg in the Environment
Source: US EPA, (1997)
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Hg species Bio –chemical property
Hg0 It is relatively inert and non-toxic.in vapour form it is toxic.
Hg2+ Toxicity is low
RHg+(Organo-mercurial)
Highly toxic cause’s irreversible nerve and brain damage can be stored in tissue. Abortion of baby affecting foetal .Borned baby suffer mental fat retardation, convulsion cerebral palsy
R2Hg(diorgano-mercurials)
Low toxicity but in acid medium converted to organo mercurials
HgS Insoluble, adsorbed in soil
Table: species of Mercury and their toxicity
Source: Das, 2005
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Fate of selenite in soil (1:10 water extract)Heavy metal load field experiment: Dr. Imre Kádár, Nagyhörcsök
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1993 1993 2003
oxidationselenite
selenate
organic selenium
Conclusion: selenite will be oxidised in soil to selenate selenate more available for plants (it is analogous to sulphate) risk of leaching
selenite
selenate
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Basic facts of Cr :
• Chromium (Cr) discovered first by the French chemist Vanquelin in 1798 from red lead ore in the Siberia.
• Cr is a transitional element in the group VI B.• Cr (VI) is most toxic usually occurs associated with
oxygen as chromate (CrO42-) or dichromate (Cr2O7
2-) oxyanions. Most mobile species.
• Cr (III) less toxic, less mobile & mainly found bound to organic matter in soil & aqueous environment.
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• Besides organic Cr (III) are known to form complexes with inorganic ligands (OH-, SO2
-, NO3- and CO3
2-). Organically complexed (citric and fulvic acids) Cr (III) prevented from precipitation even upto pH 7.5.
• Hence in most natural systems Cr (VI) occurred as CrO4
2- and Cr (III) present as hydroxides and various organic complexes.
• Cr (VI) is a strong oxidising agent & reduced by appropriate electron donor
HCrO4- + 7H+ + 3e- → Cr3+ + 4H2O←
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Reactions in Soil – Water System
• In most natural systems, hexavalent Cr6+ present as CrO4
2- & major trivalent Cr3+ species include hydroxides & various organic complexes.
• Cr undergoes various chemical & biological reactions in natural system that govern speciation & in turn, environmental behaviour.
• Important among these reactions includeOxidation or reductionPrecipitation or dissolution andAdsorption or desorption
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Cr in water
Leachate
Kinetics of Redox TransformationCr3+ Cr6+
Precipitation Dissolution
Adsorption & Desorption
Water Cr3+ & Cr6+
Predicted Cr concentration
A simple scheme involving reactions of Cr in soil & water systems
Source: Rai et al., 1989
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Effect of Cr on plant growth and development
Process Crop/plant Effect
Germination Bushbean, Lucerne, Mungbean, Sugarcane
Reduced germination percentage & reduced bud sprouting
Root growth Rice, Mungbean, Sorghum
Decrease in root length & dry weight, increase in root diameter & root hairs. Proportional variation in
cortical & pith tissue layers.
Shoot height Rice, Bushbean Reduction in plant height
Yield & Dry matter
production
Cauliflower, Cabbage, Radish, Bushbean,
Maize, Finger Millet
Upto 50% reduction in yield. Reduced number of flowers per
plant. Reduced grain weight. Increased seed deformity. Reduced
pod weight.
Source: Patel et al., 1992
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Source: Sherman, 2002
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Soil Heavy metal (ppm)
Available TOTAL
Pb Cf Cr Pb Hg Cd Cr
Surface 1.8 0.02 0.6 43.8 4.6 9.6 23.2
Sub surface 2.3 0.04 0.04 40.3 3.8 10.1 19.8
Table: Heavy Metal Pollution Through Sewage Water
Source: Som et al. (1994)
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Feer‘s Disease (acrodynia) exanthema due to Hg Toxicity
Picture Source: www.who.int/ceh
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Source of
Exposure
Methyl mercury
(MeHg) (μg/day)
Inorganic Hg Salts (Hg+
+) (μg/day)
Elemental Hg (Hg0)
(μg/day) Foods (non-fish) Negligible 0.9 Negligible
Commercial fish 6 <1 Negligible
Sport fish No population-based data
available
No population-based data
available
Negligible
Public supply
water Negligible <<4 Negligible
Private wells Negligible 0.4-4 0.006-0.03
Outdoor air Negligible Negligible 0.04 - 0.2
Indoor air Negligible Negligible No population based data
available Soil ingestion Negligible >3 Negligible
Dental amalgams Negligible Negligible .3-17
Table: 10 Sources and Estimates of Daily Human Exposures to Mercury
Source: Charles, 2000
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Elements Plant species Max. reported
conc. (mg/kg)
Cadmium Thlapsi caerulescens 500
Copper Ipomoea alpina, 12300
Cobalt Haumaniuastrum robertii 10200
Lead Thlapsi rotundifolium, Brassica juncea, Zea mays 8200
Nickel Alyssum lesbiacum, Sebertia acuminata 47500
Zinc Thlapsi caerulescens, Brassica oleracea, B.
campestris
51600
Selenium Brassica juncea, B. napus 900
Chromium Brassica juncea, Helianthus annus 1400
Table: 13 Important hyperaccumulators for metal remediation
Surce: Sarkar, 2005
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Lead
Lead is by far the most common contaminant of soils.
Lead in soil is virtually a permanent resident. Organic matter,
especially, will bind and hold itself in other metals very
effectively.
Sources: Number one source contamination: lead-based paint
Other sources: gasoline exhaust
motor oil
automobile tires
industrial activity
coal combustion, and pesticides.
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Mercury• Mercury occurs in two forms:
- organic
- inorganic
• Inorganic forms most often occur when mercury is combined
with chlorine, sulfur or oxygen.
• Organic forms occur when mercury combines with carbon.
Sources: Metallic forms of mercury are not absorbed by plants, but
are converted by microorganisms to organic forms such
as methyl mercury, which are taken up by plants.
Environmental sources include thermometers, pesticides,
metallurgy, and vapors from burning coal and other
fuels.
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Mercury in Plants• The uptake of mercury:
- decreases growth
-induces disorientation of roots and shoots, plant tissue, and finally the cell wall.
• A major portion of Mercury is tightly bound and remains in the roots.
Lead in Plants• Lead in plants:
- Absorbed through roots
- Lead builds up in both leaf and root tissue
- Causes lower concentration of chlorophyll
- Lead compounds absorb UV light
- Plants biomass declines, which includes roots, shoots, and fruits.
Toxic Effect of Hg and Pb in Plants
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Boreysza, Fabritus,Laures, 2006
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Source: Arsenic is a new terror; Asit Kumar Roy; Desh, 2004
DRAWDOWN
Radius of influence
Cone of Depression
WTVadose zone
Arsenopyrite
Darcy’s Law
Pitticite
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Effect of Arsenic Pollution
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Crop Arsenic conc. (mg/kg) at harvest
Leaf Stem Root Eco. Produce
Elephant Foot yam
4.30 8.0 - 4.0
Green gram 5.10 4.9 4.7 4.3
Cowpea 4.91 5.1 5.2 2.1
Maize 3.30 6.2 5.2 2.6
Rice (boro) 10.2 5.7 5.9 10.0
Jute 3.5 8.0 6.8 4.0
Potato 3.9 9.3 - 5.9
Mustard 7.1 9.8 5.7 3.3
Ground nut 2.0 2.0 2.2 4.0
Sesame 2.0 2.0 4.0 0.6
Crops were subjected to irrigation with water containing 0.22 mg As / lit of water Soil had an Olsen-extractable arsenic content of 1.23 to 1.37 mg/kg of soil (initial)
Arsenic uptake by different plant parts of crops grown in Gotera, Chakdah
Source Source : Prof. S. K. Sanyal,2005 : Prof. S. K. Sanyal,2005
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Then what is the way out???Then what is the way out???
PHYTOREMEDIATION
THE GREEN-CURE TECHNOLOGY
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What is phytoremediation?
“Use of green plants to remove pollutants from the
environment or render them harmless.”
This concept has emerged from a broader philosophy
of Bioremediation where besides plants, soil micro-
organism are also used for amelioration of organic and
inorganic contaminants.
Source: Salt et al.(1998)
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Phytoextraction Phytodegradation Rhizofiltration Phytostabilization Phytovolatilization
Phytoremediation
D i f f e r e n t a p p r o a c h e s o f p h y t o r e m e d i a t i o n
A c c u m u l a t io n o f m e t a l s i n s h o o t t i s s u e s f o l l o w e d b y h a r v e s t i n g
U s e o f p l a n t s a n d a s s o c i a t e d m i c r o b e s t o d e g r a d e o r g a n i c p o l l u t a n t s
U s e o f p l a n t r o o t s t o a b s o r b a n d a d s o r b m e t a l s f r o m a q u e o u s w a s t e s t r e a m
R e d u c t i o n i n l e a c h i n g , r u n o f f , s o i l e r o s i o n a n d b i o a v a i l a b i l i t yo f t o x i c m e t a l s
U s e o f p l a n t s t o v o l a t i l i z e p o l l u t a n t s
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Pteris vittata (Chinese brake) – a reported hyper-accumulator for arsenic
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Disposal of hyper-accumulator plant refuse
Harvest
Incineration
Controlled disposal of ash to underground – away from root zone and aquifer
Phytomining
Jade green alkaloid from cut stem of Phyllanthus palawanensis contains 88,580 µg Ni g-1 dry weight
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Contents of some heavy metals in fertilizers and sludges
Source Metal mg/kg dry material
Cd Cr Cu Pb Zn
Ammonium Niitrate (A/N)
1.1 2.5 3.6 5.4 11.7
SSP 16.6 157.0 22.6 20.6 244.0
Compound 8-10-8
4.9 54.3 8.3 3.2 97.5
Sewage Sludge 20.0 500.0 250.0 700.0 3000.0
Source: Pain et al., 1991
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Accumulation of Heavy Metals in Soil and Plant (mg/g) Zn Cu Pb Cd Cr
Soils of Dhapa 1038-1256 154-196 79-113 0.38-0.52 9.1-17.0
Spinach 320-340 60-72 60-82 0.8-2.2 6.5-15.8
CauliflowerHead
300-1100 20-30 30-90 Trace 5.2-5.7
Source: Gupta et al., 1997
Parts Zn Cu Pb Cd Cr
Brain 3.2 trace 2.9 0.4 11.3
Muscle 29.1 3.4 2.4 0.5 0.9
Liver 53.1 79.5 3.3 6.1 3.2
Kidney 62.6 8.9 11.9 12.3 14.9
Source: Bhattacharyya, 1997
Accumulation of Heavy Metals in Rohu fish (1.5 kg) on dry weight Basis (g/g)
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Effect of Heavy Metal Pollution on Microbial Diversity in soil (experiment conducted in
Portugal, 2006)
Source: Oliveira et al. (2006)
Micro-organism Contaminated soil Uncontaminated soil
2003 2004 2003 2004
Aerobic heterotrophic
bacteria (106 cfu/g)3.9 1.5 7.4 4.6
Actinomycetes (104
cfu/g)8.3 6.6 10.4 9.6
Fungi (105 cfu/g) 2.8 1.2 4.3 1.8
Asymbiotic Nitrogen
fixer (104 cfu/g)2.5 0.8 9.5 3.5
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Some of the cultivated species can also act as
efficient metal hyper-accumulators
Brassica juncea
Hordeum vulgare
Avena sativa
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Remedial / Mitigation Options1. Optimum conjunctive use of ground & surface water
[ e.g. harvested rainwater]
2. Irrigation with pond-stored groundwater – decontamination facilitated by rainfall and sedimentation
3. Recharge groundwater resource
4. Enhance water use efficiency (optimum water management)
5. Prefer low-water requiring farmer-attractive cropping sequences (especially for the lean period)
6. Increased use of FYM and other manures + green manure crops, inclusion of pulses/other legumes as well as application of appropriate amendments (Zn/Fe salts as and where applicable)
7. Cost-effective phytoremediation options
8. Creation of general awareness: Mass campaigning, holding of farmers’ day, field demonstrations, socioeconomic factors
(Source: Sanyal, 2008)
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The chemicals to which life is asked to make
its adjustment are . . . the synthetic creations
of man's inventive mind, brewed in his
laboratories, and having no counterparts in
nature.
Rachel CarsonSilent Spring