Arsenic Contamination Of Groundwater Seminar Report 2012-13 Department of Civil Engineering Indian Institute of Technology Banaras Hindu UniversityUnder the guidance of: Submitted by:Prof. Devendra Mohan Mayank Saxena 09103EN008 B.Tech, Part-IV
ABSTRACTNatural groundwater arsenic-contamination and the sufferings of people as a result, has become acrucial water quality problem in many parts of the world, particularly in Bengal delta, Bangladesh andWest Bengal (India). It has recently been recognized that As-contaminated groundwater used forirrigation may pose an equally serious health hazard to people eating food from the crops irrigated andthat As accumulating in irrigated soils poses a serious threat to sustainable agriculture in affected areas.This report reviews the nature of those threats, taking into account the natural and anthropogenicsources of arsenic pollution, areas affected and health impact of arsenic contamination of groundwater.
ACKNOWLEDGEMENTApart from one’s own effort, the success of any work largely depends on the encouragement andguidance of the others. I would like to take this opportunity to express my gratitude to the peopleinstrumental in the successful completion of this reportMy special thanks to Prof. Devendra Mohan ( Department of civil engineering,IIT-BHU) for mentoringmy report. I show my greatest appreciation to him for his tremendous support and help. I feel motivatedand encouraged after working under his guidance and without whom this project would not have beenmaterialized.I would also like to acknowledge and extend my heartiest gratitude to my classmates Mr. AyushAgarwal, Mr. Bhuvanesh Shukla and Mr. Deepak Kumar who gave important suggestions andtremendous support which was very vital for success of my report.
1. INTRODUCTIONArsenic is a chemical element with symbol As and atomic number 33. Arsenic occurs in many minerals,usually in conjunction with sulfur and metals, and also as a pure elemental crystal. Arsenic is a metalloid.It can exist in various allotropes, although only the gray form has important use in industry. Arsenic isnotoriously poisonous to multicellular life, although a few species of bacteria are able to use arseniccompounds as respiratory metabolites. Various physical and chemical properties of arsenic are asfollows-1.1 PHYSICAL PROPERTIES OF ARSENICArsenic occurs in three most common allotropes which are metallic grey, yellow and black arsenic, withgray being the most common. Gray arsenic adopts a double-layered structure consisting of manyinterlocked ruffled six-membered rings. Nearest and next-nearest neighbors form a distorted octahedralcomplex, with the three atoms in the same double-layer being slightly closer than the three atoms in thenext. This relatively close packing leads to a high density of 5.73 g/cm3. Gray arsenic is a semimetal,but becomes a semiconductor with a bandgap of 1.2–1.4 eV if amorphized. Yellow arsenic is soft andwaxy, and have four atoms arranged in a tetrahedral structure in which each atom is bound to each ofthe other three atoms by a single bond. This unstable allotrope, being molecular, is the most volatile,least dense and most toxic. Solid yellow arsenic is produced by rapid cooling of arsenic vapor, As4. It israpidly transformed into the gray arsenic by light. The yellow form has a density of 1.97 g/cm3. Phase solid Density 5.727g/cm3 Liquid density at 5.22g/cm3 m.p Sublimation Point 881K Triple point 1090K, 3628 kPa Heat of Fusion 24.44kJ/mole Heat of Vaporization 34.76kJ/mole Sublimation Point 881K Physical Properties of Arsenic
1.2. CHEMICAL PROPERTIESArsenic is a member of Va group of periodic table. It occur in nature in four oxidation states -3,0,+3,+5with -3 being most toxic and +5 being least toxic. In groundwater, Arsenic is found in only two oxidationstates i.e +3 and +5. Various chemical properties of Arsenic are summarize in the following table Symbol As Atomic number 33 Element category Metalloid Group,period,block Va,4,p Atomic weight 74.92160 Electronegativity 2.18(pauling scale) Atomic radius 119 pm Van der Waals radius 185 pm CHEMICAL PROPERTIES OF ARSENIC1.3 ARSENIC CONTAMINATION OF GROUNDWATERArsenic contamination of groundwater is a natural occurring high concentration of arsenic in deeperlevels of groundwater. As per WHO, maximum permissible limit of arsenic in groundwater is 10 µg/liter.Arsenic contamination poses a serious health hazard to about 150 million people worldwide(Ravenscroft et al. 2009). Around 110 million of those people live in ten countries in South and South-east Asia: Bangladesh, Cambodia, China, India, Laos, Myanmar, Nepal, Pakistan, Taiwan and Vietnam(Brammer and Ravenscroft, 2009). Recently it has also been found that As-contaminated groundwaterused for irrigation may pose an equally serious health hazard to people eating food from the cropsirrigated and that As accumulating in irrigated soils poses a serious threat to sustainable agriculture inaffected areas. Arsenic is found in nature in soils and rocks, natural waters and organisms. It is mobilizedthrough a combination of natural processes such as weathering reactions, biological activity and volcanicemissions as well as through a range of anthropogenic activities. Most environmental As problems arethe result of mobilization under natural conditions. However, man has had an important additional
impact through mining activity, combustion of fossil fuels, the use of arsenical pesticides, herbicides andcrop desiccants.2. DISTRIBUTION OF ARSENIC2.1 CONTINENT-WISE DISTRIBUTION2.1.1 ASIAMain areas affected from arsenic contamination of groundwater in Asia are Xinjiang, Liaoning, Jilin,inner Mongolia, Ningxia, Shanxi, Jhelum basin (Pakistan), Bangladesh, Nepal, Guizhou (China), Taiwan,Hanoi (Vietnam), Myanmar, West Bengal (India), Uttar Pradesh (India) , Cambodia, Ronphibun(Thailand), Gujarat (India) (Chakraborti et al,2002). DISTRIBUTION OF ARSENIC IN ASIA1) Xinjiang; (2) Jilin; (3) Liaoning; (4) inner Mongolia; (5) Ningxia; (6) Shanxi, all foregoing in China; (7) Jhelum, Pakistan; (8)Pakistan; (9) Bangladesh; (10) Nepal; (11) Guizhou, China; (12) Taiwan; (13) Hanoi, Vietnam; (14) Myanmar; (15) Lao PDR;(16) WB, India; (17) Cambodia; (18) Ronphibun, Thailand.
2.1.2 EUROPEIn Europe, problem of arsenic contamination of groundwater is less as compared to Asia. MajorEuropean countries affected from this problem are Hungary, Romania and South-west Finland. InHungary concentration of arsenic in groundwater is 1-174 µg.L-1, in Romania, concentration is about 1-176 µg.L-1 (Sharma and Sohn, 2009).2.1.3 AUSTRALIAAustralia is a country rich in minerals that constitute a significant source of arsenic contamination to theenvironment, in addition to anthropogenic sources, such as mining activities and pesticide usage. In1991, survey data revealed elevated levels of arsenic in surface water and groundwater of Victoria(Mukherjee et al, 2006).2.1.5 NORTH AMERICASome locations in the United States, such as Fallon, Nevada, have long been known to havegroundwater with relatively high arsenic concentrations (in excess of 0.08 mg/L). Even some surfacewaters, such as the Verde River in Arizona, sometimes exceed 0.01 mg/L arsenic, especially during low-flow periods when the river flow is dominated by groundwater discharge.( Taqueer and Quereshi, 1995).Other Affected areas in North America are Hermosillo, Yaqui river watershed, Valle del Guadiana,Morales in San Luis Potosi city, Puebla state, Taxco, Pol Chucabkatun, Luna-Sen, Salamanca, Acambaro,Zacatecas, Santa Ma. De la Paz, Puebla state (Bundschuh et al, 2012).2.1.4 SOUTH AMERICAAreas of South America affected from arsenic contamination are Chile, Brazil, Argentina, Peru, Ecuador,Tambo river and Papallacta lake area, Tumbaco, Locumba Valley, Quebrada de Camarones, TatioGeothermal springs, upper Pilcomayo river basin, Garayalde ( Uruguay), Santa Barbara dist. , Rimac riverbasin, Geothermal water from EL Carchi, Imbabura, Pichincha, Cotopaxi, Puno, Lluta and Azata valleys,Morococha mining region (Bundschuh et al, 2012).
DISTRIBUTION OF ARSENIC IN SOUTH AMERICA(76) Loa riverbasin/Atacamadesert, (77) Tatiogeothermal springs,(78) Coquimbo,Valle del Elqui,(79) Maipu river basin;Bolivia: (80) El Alto(LaPaz), (81) Oruro,(82) Poopó basin, (83) North ofPotosí dept., (84) Upper Pilcomayoriver basin; (85) Lipéz and south ofPotosí dep.; Argentina:(86) NWArgentine Andean highland, e.g.San Antonio de Los Cobres andmany other localities, (87) Chaco plain,(88) Pampa plain, (89)Copahue,(90) Garayalde and Camarones(Chubut prov.); Uruguay: (91) San Josédept.; Brazil: Minas Gerais st.: (92)Nova Lima dist., (93) SantaBárbaradist., (94) Ouro Preto/Mariana dist. (63) El diamantegold mine; Caldas dep.; Ecuador: (64) Tamboriver and Papallacta lake area(Quijos county,Napo prov.), (65) Guayllabamba, (66)Tumbaco, (67) Geothermal waters from ElCarchi, Imbabura, Pichincha, Cotopaxi,andTungurahua prov.; Peru: (68)Morococha miningregion/La Oroya smelting complex (Yauli prov,Junin dep.), (69) Rímac river basin,(70)Huaytará prov. (Huancavélica dep.), (71) Puno(Puno dep.), (72) Locumba valley (Tacna dep.;Ilo city water supply), (74) Arica area(Llutaand Azapavalleys, (75) Quebradade Camarones (73)Tacna area (SamaQuebrada de la Yarada)
2.1.6 AFRICAAreas affected from arsenic contamination in Africa are Obuasi and Bolgatunga regions of Ghana(Smedley, 1996). Other areas are Yatenga, Ankobra basin, Offin basin, Ekondo Titi, Okavango Delta(Ravenscroft, 2007) DISTRIBUTION OF ARSENIC IN AFRICA
2.2 DISTRIBUTION OF ARSENIC IN INDIAN SUB-CONTINENT2.2.1 PAKISTANAreas affected from arsenic contamination in Pakistan include Manchar Lake Jamshoro (Sindh), someparts of Ravi basin, Sialkot, Kasur city, Muzaffargarh, Multan, Karachi (Azizullah et al, 2011). Location Conc. Of Reference -1 As(in ug.L ) Various spots of Karachi Well water of Multan Muzzafargarh Manchar Lake2.2.2 SRI LANKAAreas affected from arsenic contamination in SriLanka are Rajarata, Anuradhapura and some parts ofColombo (Jayasumana et al, 2007).2.2.3 NEPALMajor areas affected from arsenic contamination in Nepal are Nawalparasi, Bara, Parsa, Rautahat,Rupandehi, Kapilvastu, Rautahat, and Kailali with concentration between 50-2621 µg/l (Pokhrel et al,2007).2.2.4 BANGLADESHMajor areas affected from arsenic contamination are Sylhet, Brahmanbaria, Mymensingh, Narayanganj,Sherpur, Bogra, Netrokona, Kishoreganj, Meherpur, Thakurgaon, Moulavibazar, Comilla, Madaripur,Chittagong, Rangamati, Khulna, Thakurgaon, Panchagarh, Sirajganj, Rangpur.
DISTRIBUTION OF ARSENIC IN BANGLADESH (adapted from Chakraborti et al, 2007)
2.2.5 INDIA184.108.40.206 WEST BENGAL Malda, Murshidabad, Nadia, North Parganas, Parganas, Bardhaman, Howrah, Hoogly and Kolkata haveconcentration more than 300 µg/l. Kooch Bihar, Jalpaiguri, Darjeeling, North Dinajpur and SouthDinajpur have concentration about 50µg/l (Chakraborti et al, 2007). DISTRIBUTION OF ARSENIC IN WEST BENGAL (adapted from Chakraborti et al, 2001)
220.127.116.11 UTTAR PRADESHMain areas affected from arsenic contamination in Uttar Pradesh are Varanasi, Gazipur and ballia. Thearea and population of the 3affected districts are 11450 km2 (4.8 % of the total area of UP) and8.7million, approximately 5.3 % of the total population of UP (Chakraborti et al).18.104.22.168 BIHARMain areas affected from arsenic contamination in Bihar are Chakani village (Brahampur) and Baraharablock in Buxar district. There is also a probability of arsenic contamination in districts close to arseniccontaminated Tarai region of Nepal.22.214.171.124 OTHERSOthers areas contaminated from arsenic in India are Sahibganj district of Jharkhand, Imphal East, ImphalWest, Thoubal and Bishnupur (Manipur) (Chakraborti et al), Rajnandgaon and Kanker District(Chattisgarh) (Shukla et al, 2009).3. SOURCES OF ARSENIC3.1 ARSENIC MOBILIZATION MECHANISMFour mechanisms have been proposed for the mobilization of arsenic into ground water Reductive dissolution Alkali desorption Geothermal action Sulphide oxidation3.1.1 REDUCTIVE DISSOLUTIONIron (III) oxyhydroxides are of particular environmental relevance because they often occur as finegrained particles and exhibit high reactive surfaces. The Fe(II)/Fe(III) redox couple is an importantelectron-transfer mediator for many biological and chemical species. As a consequence, the stability ofFe(III) oxyhydroxides in soils exerts a major control on mobility of both organic and inorganic pollutantssuch as arsenic. Iron-reducing bacteria — which are present in waterlogged soils and aquifers — couplethe oxidation of organic matter with the reduction of various Fe(III) oxyhydroxides for their metabolism.A direct consequence of Fe(III) reduction is the associated trace metal release into soil solution (Fakih etal,2009).
3.1.2 ALKALI DESORPTIONLaboratory studies show that arsenic adsorbed to iron, manganese and aluminum oxides and clayminerals may be desorbed at pH >8.0, leaving the carrier phase as a solid. The best-documentedexample comes from the southwest USA (Baxfield and Plummer, 2003), and others come fromOklahoma, Spain, China and from volcanic deposits in Argentina (Nicolli et al, 1989).3.1.3 SULPHIDE OXIDATIONArsenic sulfide minerals such as orpiment and realgar are of significant economic interest in manymining operations because of their role as reliable indicators of gold mineralization .These minerals arealso of great environmental interest because the oxidative dissolution of these minerals can potentiallyincrease the concentrations of As in natural water ( Lengke and Tempel, 2004). The proposed overallreactions of arsenic sulfide oxidation are written as:As2S3 + 7O2 + 6H2O 2HAsO42- + 3SO42- + 10H+AsS + 2.75O2 + 2.5H2O HAsO42- +SO42- + 4H+3.1.4 GEOTHERMAL ACTIONMixing of geothermal solutions and fresh ground water can lead to high arsenic concentrations in somelocations (Smedley and Kinniburgh, 2002).3.2 MAJOR AREAS CONTAMINATED FROM ARSENIC AND ARSENICMOBILIZATION MECHANISM INVOLVEDContaminated Areas Mechanism involved ReferencesWest Bengal Reductive dissolution Harvey et al,2004Bangladesh Reductive dissolution and in Harvey et al,2004; some parts geochemical Anawar et al 2001South-West USA Alkali desorption Baxfield and Plummer, 2003Perth (Australia) Sulphide Oxidation Appleyard et al,2006
Mid-West USA Reductive Dissolution Kelly et al,2005Spain Alkali Desorption Ravenscroft 2007Argentina Alkali Desorption Nicolli et al,1989Danube (Europe) Reductive dissolution Kelly et al, 2005China Alkali desorption Ravenscroft 2007Chile (South America) Geothermal activity Smith et al,1998Tibet plateau Geothermal activity Ravenscroft 2007Ghana (Africa) Sulphide oxidation Smedley 19953.3 ANTHROPOLOGICAL ACTIVITIES LEADING TO ARSENICCONTAMINATION OF GROUNDWATERMany compounds of arsenic are used in various field which have a potential to spread arseniccontamination. Some of the major compounds are:3.3.1 CHROMATED COPPER ARSENATEChromated copper arsenate (CCA) has been long used for treating wood in order to increase its lifetimein outdoor applications. It had been observed that the chemical and structural forms of either Cr or As inthe exposed wood are the same as in freshly treated material (Nico et al,2004). The leaching of dislodgeabled residues of CCA-preserved wood with simulated biological fluids (sweat or gastric juice) indicatedthe main presence of free As(V) anionic species. Another source of As comes from CCA-impregnatingplants, whose soils may contain high pools of potential contamination.3.3.2 4-HYDROXY-3-NITROBENZENE ARSONIC ACID (ROXARSONE)The common use of antibiotic additive Roxarsone is in poultry farm to increase the chicken weight.However As is largely excreted and consequently poultry litter can contain high As levels (Villaescusaand Bollinger,2007): up to 40 mg/kg (dry weight). Moreover such As from poultry litter is easily watersoluble with 70–90% extraction rate (Garbarino et al.2003; Rutherford et al. 2003), and transformed toAs(V) due to both photo degradation and mineralization in the presence of nitrate and organic matter(Bednar et al. 2003).
3.3.3 MONOSODIUM METHANEARSONATE (MSMA)It a common arsenical herbicide used in golf course green treatment, led to a systematic monitoring ofrelated soils and the water percolating through these soils .Presumably due to microbial activity in thesoil, MSMA was found to be transformed to As(V),As(III), MMA and DMA; after 14 weeks, almost20% ofinorganic As originating from MSMA can percolate below the rhizosphere (Villaescusa andBollinger,2008). Other anthropological causes of arsenic contamination are not yet verified but it is hypothesized that excessive use of groundwater create an environment which favors arsenic mobilization through soil. Improper disposal of mining wastes also causes the groundwater contamination in mining areas.4. IMPACTS OF ARSENIC CONTAMINATIONBefore discussing about the impacts of arsenic contamination let us first discuss about the toxicity oftwo arsenic species: As(III) and As(IV) present in groundwater.4.1 TOXICITY OF ARSENICIt is commonly accepted that inorganic As(III) compounds are approximately 60–80 times more toxic tohumans than As(V) ones (Villaescusa and Bollinger,2008). The acute toxicity of arsenic is related to itschemical form and oxidation state. Toxicity of any chemical species is measured in LD50 (LD50 withrespect to any biological species is the amount required to kill 50% of a given test species.). Toxicity levelof some arsenic compounds are shown in the table.CHEMICAL SPECIES (sex) LD50 (mg/kg) REFERNCESArsenite Mouse (male) 8 Bencko et al,1978Arsenite Hamster (male) 8 Petrick et al,2001Arsenate Mouse (male) 22 Bencko et al,1978Arsenobetaine Mouse (male) >4260 Kaise et al, 1985
Arsenic trioxide Mouse (male) 26-48 Harrison et al, 1958MMA Hamster (male) 2 Petrick et al,2001DMA Mouse (male) 648 Kaise et al, 1985TMAO Mouse (male) 5500 Kaise et al, 19854.1.1 MECHANISM OF PENTAVALENT ARSENIC TOXICITYArsenate can replace phosphate in many biochemical reactions because they have similar structure andproperties (Hughes, 2001). For example: Arsenate reacts in vitro with glucose and gluconate to formglucose-6-arsenate and 6- arsenogluconate, respectively. These compounds resemble glucose-6-phosphate and 6- phosphogluconate, respectively. Arsenate can also replace phosphate in the sodium pump and the anion exchange transport system of the human red blood cell (Hughes, 2001). Arsenate uncouples in vitro formation ofadenosine-5-triphosphate (ATP) by a mechanism termed arsenolysis. Depletion of ATP by arsenate has been observed in cellular systems. ATP levels are reduced in human erythrocytes (Winski and Carter,1998) after in vitro exposure to arsenate.4.1.2 MECHANISM OF TRIVALENT ARSENIC TOXICITYSpecific functional groups within enzymes, receptors or coenzymes, such as thiols or vicinal sulfhydryls,have a major role in the activity of these molecules. Trivalent arsenic readily react in vitro with thesethiol-containing molecules (Hughes,2001). The binding of trivalent arsenic to critical thiol groups mayinhibit important biochemical events which could lead to toxicity. Pyruvate dehydrogenase (PDH) is amulti-subunit complex that requires lipoic acid (a dithiol) for enzymatic activity so arsenite inhibits PDHby binding to the lipoic acid which ultimately leads to the decreased production of ATP (Hughes,2001).
4.2 WHY IS ARSENIC BAD FOR HEALTH?Arsenic dissolved in water is acutely toxic and can lead to a number of health problems. Long-termexposure to arsenic in drinking-water causes increased risks of cancer in the skin, lungs, bladder andkidney. It also leads to other skin-related problems such hyperkeratosis and changes in pigmentation.Consumption of arsenic also leads to disturbance of the cardiovascular and nervous system functionsand eventually leads to death. Increased risks of lung and bladder cancer and of arsenic-associated skinlesions have been reported for consuming drinking-water with arsenic concentrations equal to orgreater than 50 parts per billion (or microgram per liter). (WHO Environmental Health Criteria).Arsenicosis, or arsenic toxicity, develops after two to five years of exposure to arsenic contaminateddrinking water, depending on the amount of water consumption and arsenic concentration in water.Initially, the skin begins to darken (called diffuse melanosis). This happens first in the palms. Diffusemelanosis leads to spotted melanosis, when darkened spots begin to appear on the chest, back andlimbs, although the latter is what is usual among people, and so is taken to be an early symptom. At alater stage, leucomelanosis sets in: the body begins to show black and white spots.Keratosis is the middle stage of arsenicosis. The skin, in portions, becomes hard and fibrous; it is as if thebody has broken out into hard boils, or ulcers. Diffuse or nodular keratosis on the palm of the hand orsole of the foot is a sign of moderately severe toxicity. Rough dry skin, often with palpable nodules onhands, feet and legs means severe toxicity. This can lead to the formation of gangrene, and cancer.Arsenic poisoning brings with it other complications: liver and spleen enlargement and cirrhosis of theliver; myocardial degeneration and cardiac failure; peripheral neuropathy affecting primary sensoryfunctions; diabetes mellitus and goiter. Another unfortunate and complicating fact about arsenicpoisoning, is that it generally takes from seven to 10 years sometimes longer, for the disease to berecognized. When it finally is, it may be too late to treat.SYSTEM EFFECTSkin Skin LesionsCardiovascular Blackfoot diseaseNervous Peripheral neuropathy, EncephalopathyEndocrine DiabetesRenal Proximal tubule degeneration, papillary and cortical necrosisHematological Bone marrow depression ADAPTED FROM HUGHES,2002
DRINKING WATER/FOOD NATURAL MINING/ DEPOSITS/SOILSCOALBURNING HUMAN EXPOSURE TO ARSENIC UPTAKE EXCRETION CELLULAR METABOLISM/TOXICITY ACCUMULATION CARCINOGEN NON-CARCINOGEN CHROMOSOMAL ABNORMALITIES CARDIOVASCULAR OXIDATIVE STRESS AND NON- CARDIOVASCULAR AFFECTS ABERRATIONS IN GENE EXPRESSION MODIFICATION OF CELL PROLIFERATION HUMAN EXPOSURE TO EXPOSURE AND VARIOUS MODE OF ARSENIC TOXICITY ( adapted from Roy and Saha)
CONCLUSIONThis review, based on a large number of accessible sources of information on As contamination ingroundwater suggests that arsenic contamination is highest in South and South-East Asia and lowest inAfrica. Most of the sources of arsenic contamination are natural whereas anthropological activities workas a catalyst in the mobilization of arsenic. Various mechanisms for mobilization of arsenic through soilare proposed which depends mainly upon the hydro-geochemical properties of the area. Inorganicarsenic is a carcinogen for human (not yet proved for animals) and it also causes various cardiovascularand vascular diseases to human. About 137 million people in more than 70 countries are probablyaffected by arsenic poisoning of drinking water, so it is very important to take measures to reduce thearsenic concentration in groundwater on a large scale. Reverse Osmosis filter system should be installedin households to avoid arsenic poisoning.
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MAGGY F. LENGKE1, REGINA N. TEMPEL, 2004. Geochemical modeling of arsenic sulfide oxidation kinetics in a mining environment Bethany OShea, Jerzy Jankowski, Jesmond Sammut, 2006. The source of naturally occurring arsenic in a coastal sand aquifer of eastern Australia http://en.wikipedia.org/wiki/Arsenic_contamination_of_groundwater http://en.wikipedia.org/wiki/Arsenic http://en.wikipedia.org/wiki/Arsenic_poisoning http://water.epa.gov/lawsregs/rulesregs/sdwa/arsenic/index.cfm