Sunday, 8 October 2017

EFFECTS AND CONTROL OF ENVIRONMENTAL POLLUTION FROM HEAVY METALS

KADUNA STATE UNIVERSITY, (KASU). DEPARTMENT OF CHEMISTRY, FACULTY OF SCIENCE. A SEMINAR RESEARCH ON “EFFECTS AND CONTROL OF ENVIRONMENTAL POLLUTION FROM HEAVY METALS” BY SULEIMAN MUHAMMAD KASU/13/CHM/1044 ABSTRACT Heavy metals are naturally occurring elements that have a high atomic weight and a density at least 5 times greater than that of water. Their multiple industrial, domestic, agricultural, medical and technological applications have led to their wide distribution in the environment; raising concerns over their potential effects on human health and the environment. Their toxicity depends on several factors including the dose, route of exposure, and chemical species, as well as the age, gender, genetics, and nutritional status of exposed individuals. Because of their high degree of toxicity, arsenic, cadmium, chromium, lead, and mercury rank among the priority metals that are of public health significance. These metallic elements are considered systemic toxicants that are known to induce multiple organ damage, even at lower levels of exposure. They are also classified as human carcinogens (known or probable) according to the U.S. Environmental Protection Agency, and the International Agency for Research on Cancer. This review provides an analysis of their environmental occurrence, production and use, potentials for human exposure, and molecular mechanisms of toxicity, carcinogenicity. CHAPTER ONE Introduction Pollution is the introduction of contaminants into the natural environment that cause adverse change. Pollution can take the form of chemical substances or energy, such as noise, heat or light. The components of pollution can be either foreign substances/energies or naturally occurring contaminants (reference). Pollution can be classified according to the part of environment affected, which are soil, air and water. Pollution may also be classified depending on the type of pollutants, for example heavy metal pollution where the pollutants are mainly heavy metals, where the pollutants are volatile organic compound it is known as volatile organic compound pollution (Ubwa et al., 2013). Discuss more on pollution TYPES OF POLLUTION 1.5 Air Pollution Air pollution is a type of environmental pollution in which the part of environment polluted is the air. Air pollution is the accumulation in the atmosphere of substances that, in sufficient concentrations, endanger human health or produce other measured effects on living matter and other materials. Air pollution is caused by emission of particulate matter and gases such as methane (CH4), sulfurdioxide (SO2) and oxides of nitrogen (NO)x as well as carbon monoxide (CO). Mining operations like drilling, blasting, hauling, collection and transportation are the major sources of air pollution (Oladoye and Adewuyi, 2014). Talk more 1.6 Water Pollution Water pollution is the introduction of chemical, biological and physical material into fresh or ocean that degrades the quality of the water and affects the organisms living in it. This process ranges from simple addition of dissolved or suspended solids to discharge of the most insidious and persistent toxic pollutants (such as pesticides, heavy metals, and nondegradable, bioaccumulative, chemical compounds (Ameh et al., 2014). Water pollution in coal mines occurs due to the coal content or impurities, rate of extraction, mining method, inflow rate of water and the amount of water used in mine. Once the mining activity begin, the hydrology of the area changes due to the addition of dissolved and suspended particles. The extent of water pollution is primarily due to the composition of ore deposits, structural features of the area and its surrounding and also the climate of the mining regions. It also depend on how the water enters into the mine and how it interacts with the rocks and ore in which way it is utilized in mining processes and the way it is pumped out of mines (Mahboob et al., 2014). 1.7 Soil Pollution Soil pollution is the degradation of the Earth's land surface through misuse of the soil by poor agricultural practice, mineral exploitation, industrial waste dumping, and indiscriminate disposal of urban wastes. It includes visible waste and litter as well as pollution of the soil itself (Kiran et al., 2012). Presence of heavy metals in soils has considerable impact on the environment causing severe damages thereby restricting soil use. Soil pollution caused by mining and mineral processes usually accumulate huge amount of heavy metals in waste dumps. Mining activity represent a high area of activity thus constituting a great hazard due to the presence of heavy metals related to functioning or abandoned mines (Marta et al, 2012). Discuss more Environmental Pollution Environmental pollution is the introduction of pollutants into the environment, which are generated through natural and anthropogenic activities that causes acute (short term) or chronic (long term) effects in living organisms (Bingol et al., 2010). Environmental pollution is the introduction of harmful substances into the environment which has many adverse effects on human health, agricultural productivity and natural ecosystem (Osuocha et al, 2013). Discuss more 1.4 Source of Environmental Pollution Environmental pollution caused by human activities such as industrial effluent discharge, vehicular emissions, waste incineration and mining operations have been the major sources of environmental pollution. Rapid growth of industries, population and transportation systems contribute to the increasing pollution levels. It is also known that mining, smelting and quarrying activities have created local environmental effects, these effects ranges from acute to chronic intoxications of living organisms that are exposed to the polluted environment (Ubwa et al., 2013). HEAVY METALS Heavy metals are naturally occurring elements that have a high atomic weight and a density at least 5 times greater than that of water, examples of heavy metals are Mercury (Hg), Cadmium (Cd), Arsenic (As), Chromium (Cr), Thallium (Tl), and Lead (Pb). Their multiple industrial, domestic, agricultural, medical and technological applications have led to their wide distribution in the environment; raising concerns over their potential effects on human health and the environment [2]. Their toxicity depends on several factors including the dose, route of exposure, and chemical species, as well as the age, gender, genetics, and nutritional status of exposed individuals, due to their high degree of toxicity, arsenic, cadmium, chromium, lead, and mercury rank among the priority metals that are of public health concern (reference). These metallic elements are considered systemic toxicants that are known to induce multiple organ damage, even at lower levels of exposure. They are also classified as human carcinogens according to the U.S. Environmental Protection Agency, and the International Agency for Research on Cancer (reference). Although heavy metals are naturally occurring elements that are found throughout the earth’s crust, most environmental contamination and human exposure result from anthropogenic activities such as mining and smelting operations, industrial production and use, and domestic and agricultural use of metals and metal-containing compounds [4–7]. Environmental contamination can also occur through metal corrosion, atmospheric deposition, soil erosion of metal ions and leaching of heavy metals, sediment re-suspension and metal evaporation from water resources to soil and ground water [8]. Heavy Metal Toxicity Heavy metal toxicity is the degree to which heavy metals can harm or affect humans or animals. Acute toxicity involves harmful effects through short-term exposure while chronic toxicity involves harmful effects over an extended period of time (Garba et al., 2013). Once heavy metals are ingested, numerous health problems occur. For example, Lead causes learning disabilities, impaired protein and haemoglobin synthesis and shorten the lifespan of red blood cells which leads to severe anaemia. Cadmium causes renal failure, accumulation in the bone which causes calcium loss and malfunctioning of peripheral and central nervous systems. Zinc causes slow growth in children, reduced fertility, headache and nausea (Mohammad et al., 2011). Arsenic toxicity causes diabetes, skin and bladder cancer (Roberge et al., 2009). Chromium toxicity is associated with allergies, skin irritation, perforation of the ear drum and respiratory track disorders (Silvia et al., 2013).Most accumulation of toxic metals is due to the ambient concentration of these metals through inhalation of dust and fumes ingestion of foods and drinks or absorption through the skin in most cases. However, most classical toxicities associated with metals have come through massive pollution of the environment through industrial activities (Tobias et al., 2013). 1.10 Sources of Heavy Metals. There are two main sources of heavy metals in the environment. These sources are natural or anthropogenic sources. Natural Sources: This is due to natural phenomenon such as weathering of rocks, volcanic activities, earth quake, forest fire and ocean sprays. The natural phenomenon releases heavy metals and other organic pollutants into the environment (Kennish, 1992). Anthropogenic Sources: This is due to human activities such as metal processing in refineries, domestic wastewater effluent, agricultural waste, transportation and combustion of fossil fuel and industrial sources include petroleum combustion, nuclear power stations and high tension lines, plastics, textiles, microelectronics, wood preservation and paper processing plants [9–11].. These activities release heavy metals and other pollutants which settle in the environment (Moore et al., 2011). CHAPTER TWO Heavy metals are generally defined as metals with relatively high densities, atomic weights, or atomic numbers. In metallurgy, for example, a heavy metal may be defined on the basis of density, whereas in physics the distinguishing criterion might be atomic number, while a chemist would likely be more concerned with chemical behaviour (reference). The earliest known metals—common metals such as iron, copper, and tin, and precious metals such as silver, gold, and platinum—are heavy metals. From 1809 onwards, light metals, such as magnesium, aluminium, and titanium, were discovered, as well as less well-known heavy metals including gallium, thallium, and hafnium (reference). Heavy metals are either essential nutrients (typically iron, cobalt, and zinc), or relatively harmless (such as ruthenium, silver, and indium), but can be toxic in larger amounts or certain forms. Other heavy metals, such as cadmium, mercury, and lead, are highly poisonous. Potential sources of heavy metal poisoning include mining and industrial wastes, agricultural runoff, occupational exposure, and paints and treated timber. (Reference) Physical and chemical characterizations of heavy metals need to be treated with caution, as the metals involved are not always consistently defined. As well as being relatively dense, heavy metals tend to be less reactive than lighter metals and have much less soluble sulfides and hydroxides (Reference). While it is relatively easy to distinguish a heavy metal such as tungsten from a lighter metal such as sodium, a few heavy metals such as zinc, mercury, and lead have some of the characteristics of lighter metals, and lighter metals such as beryllium, scandium, and titanium have some of the characteristics of heavier metals (reference). Heavy metal pollution is an inorganic chemical hazard, which is mainly caused by lead (Pb), chromium (Cr), arsenic (As), cadmium (Cd), mercury (Hg), zinc (Zn), copper (Cu), cobalt (Co), and nickel (Ni) [1]. Five metals among them, Pb, Cr, As, Cd, and Hg, are the key heavy metal pollutants. These heavy metals are classified as strong carcinogens by the International Agency for Research on Cancer [2]. High level of heavy metal exposure can also cause permanent intellectual and developmental disabilities, including reading and learning disabilities, behavioural problems, hearing loss, attention problems, and disruption in the development of visual and motor function [2]. Among various types of pollution, heavy metal pollution is a crucial environmental problem. Some traditional pollutants, such as sulfur dioxide and carbon dioxide, have been put under control, but heavy metal pollution, which poses even greater risks to public health, is yet to gain policy makers’ attention (reference). Effects of heavy metals contaminations The effects of heavy metal-induced toxicity and carcinogenicity involve many mechanistic aspects, some of which are not clearly elucidated or understood (reference). However, each heavy metal is known to have unique features and physio-chemical properties that confer to its specific toxicological mechanisms of action (reference). This review provides an analysis of the environmental occurrence, production and use, potential for human exposure, and molecular mechanisms of toxicity, and carcinogenicity of arsenic, cadmium, chromium, lead, and mercury. Arsenic Environmental Occurrence, Industrial Production and Use Arsenic (As) is a ubiquitous (widespread or very prevalent) element that is detected at low concentrations in virtually all environmental matrices [33]. The major inorganic forms of arsenic include the trivalent arsenite and the pentavalent arsenate. The organic forms are the methylated metabolites – monomethylarsonic acid (MMA), dimethylarsinic acid (DMA) and trimethylarsine oxide. Environmental pollution by arsenic occurs as a result of natural phenomena such as volcanic eruptions and soil erosion, and anthropogenic activities [33]. Several arsenic-containing compounds are produced industrially, and have been used to manufacture products with agricultural applications such as insecticides, herbicides, fungicides, algaecides, sheep dips, wood preservatives, and dye-stuffs. They have also been used in veterinary medicine for the eradication of tapeworms in sheep and cattle [34]. Arsenic compounds have also been used in the medical field for at least a century in the treatment of syphilis, yaws, amoebic dysentery, and trypanosomaiasis [34,35]. Arsenic-based drugs are still used in treating certain tropical diseases such as African sleeping sickness and amoebic dysentery, and in veterinary medicine to treat parasitic diseases, including filariasis in dogs and black head in turkeys and chickens [35]. Recently, arsenic trioxide has been approved by the Food and Drug Administration as an anticancer agent in the treatment of acute promeylocytic leukemia [36], its therapeutic action has been attributed to the induction of programmed cell death (apoptosis) in leukemia cells [24]. Arsenic Potential for Human Exposure It is estimated that several million people are exposed to arsenic chronically throughout the world, especially in countries like Bangladesh, India, Chile, Uruguay, Mexico, Taiwan, where the ground water is contaminated with high concentrations of arsenic (reference). Exposure to arsenic occurs through oral route (ingestion), inhalation, dermal contact, and the parenteral route to some extent [33,34,37]. Arsenic concentrations in air range from 1 to 3 ng/m3 in remote locations (away from human releases), and from 20 to 100 ng/m3 in cities, in water the concentration is usually less than 10µg/L, although higher levels can occur near natural mineral deposits or mining sites while arsenic concentration in various foods ranges from 20 to 140 ng/kg [38]. Natural levels of arsenic in soil usually range from 1 to 40 mg/kg, but pesticide application or waste disposal can produce much higher values [25]. Mechanisms of Arsenic Toxicity and Carcinogenicity Analyzing the toxic effects of arsenic is complicated because the toxicity is highly influenced by its oxidation state and solubility, as well as many other intrinsic and extrinsic factors [45]. Several studies have indicated that the toxicity of arsenic depends on the exposure dose, frequency and duration, the biological species, age, and gender, as well as on individual susceptibilities, genetic and nutritional factors [46]. Most cases of human toxicity from arsenic have been associated with exposure to inorganic arsenic. Inorganic trivalent arsenite (AsIII) is 2–10 times more toxic than pentavalent arsenate (AsV) [5]. By binding to thiol or sulfhydryl groups on proteins, As (III) can inactivate over 200 enzymes. This is the likely mechanism responsible for arsenic’s widespread effects on different organ systems. U did not talk abt d ability of arsenic to cause cancer Cadmium Environmental Occurrence, Industrial Production and Use Cadmium (Cd) is a heavy metal of considerable environmental and occupational concern. It is widely distributed in the earth's crust at an average concentration of about 0.1 mg/kg. The highest level of cadmium compounds in the environment is accumulated in sedimentary rocks, and marine phosphates containing about 15 mg cadmium/kg [88]. Cadmium is frequently used in various industrial activities. The major industrial applications of cadmium include the production of alloys, pigments, and batteries [89]. Although the use of cadmium in batteries has shown considerable growth in recent years, its commercial use has declined in developed countries in response to environmental concerns. In the United States for example, the daily cadmium intake is about 0.4µg/kg/day, less than half of the U.S. EPA’s oral reference dose [90]. This decline has been linked to the introduction of stringent effluent limits from electroplating works and, more recently, to the introduction of general restrictions on cadmium consumption in certain countries (reference). Potential of Cadmium for Human Exposure The main routes of exposure to cadmium are through inhalation or cigarette smoke, and ingestion of food. Skin absorption is rare. Human exposure to cadmium is possible through a number of several sources including employment in primary metal industries, eating contaminated food, smoking cigarettes, and working in cadmium-contaminated work places, with smoking being a major contributor [91, 92]. Other sources of cadmium include emissions from industrial activities, including mining, smelting, and manufacturing of batteries, pigments, stabilizers, and alloys [93]. Cadmium is also present in trace amounts in certain foods such as leafy vegetables, potatoes, grains and seeds, liver and kidney, and crustaceans and mollusks [94]. In addition, foodstuffs that are rich in cadmium can greatly increase the cadmium concentration in human bodies examples are liver, mushrooms, shellfish, mussels, cocoa powder and dried seaweed. An important distribution route is the circulatory system whereas blood vessels are considered to be main stream organs of cadmium toxicity. Chronic inhalation exposure to cadmium particulates is generally associated with changes in pulmonary function and chest radiographs that are consistent with emphysema [95]. Workplace exposure to airborne cadmium particulates has been associated with decreases in olfactory function [96]. Several epidemiologic studies have documented an association of chronic low-level cadmium exposure with decreases in bone mineral density and osteoporosis [97–99]. Molecular Mechanisms of Cadmium Toxicity and Carcinogenicity Cadmium is a severe pulmonary and gastrointestinal irritant, which can be fatal if inhaled or ingested. After acute ingestion, symptoms such as abdominal pain, burning sensation, nausea, vomiting, salivation, muscle cramps, vertigo, shock, loss of consciousness and convulsions usually appear within 15 to 30 min [105]. Acute cadmium ingestion can also cause gastrointestinal tract erosion, pulmonary, hepatic or renal injury and coma, depending on the route of poisoning [105, 106]. Chronic exposure to cadmium has a depressive effect on levels of norepinephrine, serotonin, and acetylcholine [107]. Rodent studies have shown that chronic inhalation of cadmium causes pulmonary adenocarcinomas [108, 109]. It can also cause prostatic proliferative lesions including adenocarcinomas, after systemic or direct exposure [110]. Chromium Environmental Occurrence, Industrial Production and Use Chromium (Cr) is a naturally occurring element present in the earth’s crust, with oxidation states (or valence states) ranging from chromium (II) to chromium (VI) [129]. Chromium compounds are stable in the trivalent [Cr(III)] form and occur in nature in this state in ores, such as ferrochromite. The hexavalent [Cr(VI)] form is the second-most stable state [28]. Elemental chromium [Cr(0)] does not occur naturally. Chromium enters into various environmental matrices (air, water, and soil) from a wide variety of natural and anthropogenic sources with the largest release coming from industrial establishments (reference). Industries with the largest contribution to chromium release include metal processing, tannery facilities, chromate production, stainless steel welding, and ferrochrome and chrome pigment production (reference). The increase in the environmental concentrations of chromium has been linked to air and wastewater release of chromium, mainly from metallurgical, refractory, and chemical industries. Chromium released into the environment from anthropogenic activity occurs mainly in the hexavalent form [Cr(VI)] [130]. Hexavalent chromium [Cr(VI)] is a toxic industrial pollutant that is classified as human carcinogen by several regulatory and non-regulatory agencies [130–132]. The health hazard associated with exposure to chromium depends on its oxidation state, ranging from the low toxicity of the metal form to the high toxicity of the hexavalent form. All Cr(VI)-containing compounds were once thought to be man-made, with only Cr(III) naturally ubiquitous in air, water, soil and biological materials. Recently, naturally occurring Cr(VI) has been found in ground and surface waters at values exceeding the World Health Organization limit for drinking water of 50 µg of Cr(VI) per liter [133]. Chromium is widely used in numerous industrial processes and as a result, is a contaminant of many environmental systems [134]. Commercially chromium compounds are used in industrial welding, chrome plating, dyes and pigments, leather tanning and wood preservation. Chromium is also used as anticorrosive in cooking systems and boilers [135, 136]. Potentials of Chromium for Human Exposure It is estimated that more than 300,000 workers are exposed annually to chromium and chromium-containing compounds in the workplace. In humans and animals, [Cr(III)] is an essential nutrient that plays a role in glucose, fat and protein metabolism by potentiating the action of insulin [5]. However, occupational exposure has been a major concern because of the high risk of Cr-induced diseases in industrial workers occupationally exposed to Cr(VI) [137]. Also, the general human population and some wildlife may also be at risk. It is estimated that 33 tons of total Cr are released annually into the environment [130]. The U.S. Occupational Safety and Health Administration (OSHA) recently set a “safe” level of 5µg/m3, for an 8 hours time-weighted average, even though this revised level may still pose a carcinogenic risk [138]. For the general human population, atmospheric levels range from 1 to 100 ng/cm3, but can exceed this range in areas that are close to Cr manufacturing [139]. Mechanisms of Chromium Toxicity and Carcinogenicity Major factors governing the toxicity of chromium compounds are oxidation state and solubility. Cr(VI) compounds, which are powerful oxidizing agents and thus tend to be irritating and corrosive, appear to be much more toxic systemically than Cr(III) compounds, given similar amount and solubility [146, 147]. Although the mechanisms of biological interaction are uncertain, the variation in toxicity may be related to the ease with which Cr(VI) can pass through cell membranes and its subsequent intracellular reduction to reactive intermediates (reference). Since Cr(III) is poorly absorbed by any route, the toxicity of chromium is mainly attributable to the Cr(VI) form (reference). It can be absorbed by the lung and gastrointestinal tract, and even to a certain extent by intact skin. The reduction of Cr(VI) is considered as being a detoxification process when it occurs at a distance from the target site for toxic or genotoxic effect while reduction of Cr(VI) may serve to activate chromium toxicity if it takes place in or near the cell nucleus of target organs [148]. If Cr(VI) is reduced to Cr(III) extracellularly, this form of the metal is not readily transported into cells and so toxicity is not observed. The balance that exists between extracellular Cr(VI) and intracellular Cr(III) is what ultimately dictates the amount and rate at which Cr(VI) can enter cells and impart its toxic effects [134]. Lead Environmental Occurrence, Industrial Production and Use Lead (Pb) is a naturally occurring bluish-gray metal present in small amounts in the earth’s crust. Although lead occurs naturally in the environment, anthropogenic activities such as fossil fuel burning, mining, and manufacturing contribute to the release of high concentrations. Lead has many different industrial, agricultural and domestic applications. It is currently used in the production of lead-acid batteries, ammunitions, metal products (solder and pipes), and devices to shield X-rays. An estimated 1.52 million metric tons of lead were used for various industrial applications in the United Stated in 2004. Of that amount (reframe the sentence), lead-acid batteries production accounted for 83 percent, and the remaining usage covered a range of products such as ammunitions (3.5 percent), oxides for paint, glass, pigments and chemicals (2.6 percent), and sheet lead (1.7 percent) [165, 166]. Potentials of Lead for Human Exposure Exposure of lead occurs mainly through inhalation of lead-contaminated dust particles or aerosols, and ingestion of lead-contaminated food, water, and paints [173, 174]. Adults absorb 35 to 50% of lead through drinking water and the absorption rate for children may be greater than 50%. Lead absorption is influenced by factors such as age and physiological status. In the human body, the greatest percentage of lead is taken into the kidney, followed by the liver and the other soft tissues such as heart and brain, however, the lead in the skeleton represents the major body fraction [175]. The nervous system is the most vulnerable target of lead poisoning. Headache, poor attention spam, irritability, loss of memory and dullness are the early symptoms of the effects of lead exposure on the central nervous system [170, 173]. Molecular Mechanisms of Lead Toxicity and Carcinogenicity There are many published studies that have documented the adverse effects of lead in children and the adult population (reference). In children, these studies have shown an association between blood level poisoning and diminished intelligence, lower intelligence quotient-IQ, delayed or impaired neurobehavioral development, decreased hearing acuity, speech and language handicaps, growth retardation, poor attention span, and anti social and diligent behaviors [178, 179, 184, 185]. In the adult population, reproductive effects, such as decreased sperm count in men and spontaneous abortions in women have been associated with high lead exposure [186, 187]. Acute exposure to lead induces brain damage, kidney damage, and gastrointestinal diseases, while chronic exposure may cause adverse effects on the blood, central nervous system, blood pressure, kidneys, and vitamin D metabolism [173, 174, 178, 179, 184–187]. How does it cause cancer? Mercury Environmental Occurrence, Industrial Production and Use Mercury (Hg) is a heavy metal belonging to the transition element series of the periodic table. It is unique in that it exists or is found in nature in three forms (elemental, inorganic, and organic), with each having its own profile of toxicity [207]. At room temperature elemental mercury exists as a liquid which has a high vapour pressure and is released into the environment as mercury vapour. Mercury also exists as a cation with oxidation states of +1 (mercurous) or +2 (mercuric) [208]. Methylmercury is the most frequently encountered compound of the organic form found in the environment, and is formed as a result of the methylation of inorganic (mercuric) forms of mercury by microorganisms found in soil and water [209]. Mercury is a widespread environmental toxicant and pollutant which induces severe alterations in the body tissues and causes a wide range of adverse health effects [210]. Both humans and animals are exposed to various chemical forms of mercury in the environment, these include elemental mercury vapour (Hg0), inorganic mercurous (Hg+1), mercuric (Hg+2), and the organic mercury compounds [211], this is because mercury is ubiquitous in the environment therefore humans, plants and animals cannot avoid the exposure of some form of mercury [212]. Hw does mercury cause cancer? Potentials of Mercury for Human Exposure Humans are exposed to all forms of mercury through accidents, environmental pollution, food contamination, dental care, preventive medical practices, industrial and agricultural operations, and occupational operations [215]. The major sources of chronic, low level mercury exposure are dental amalgams and fish consumption. Mercury enters water as a natural process of off-gassing from the earth’s crust and also through industrial pollution [216]. Algae and bacteria methylate the mercury entering the waterways. Methyl mercury then makes its way through the food chain into fish, shellfish, and eventually into humans [217]. Molecular Mechanisms of Mercury Toxicity and Carcingenicity The molecular mechanisms of toxicity of mercury are based on its chemical activity and biological features which suggest that oxidative stress is involved in its toxicity [220]. Through oxidative stress mercury has shown mechanisms of sulfhydryl reactivity. Once in the cell both Hg2+ and MeHg form covalent bonds with cysteine residues of proteins and deplete cellular antioxidants. Antioxidant enzymes serve as a line of cellular defence against mercury compounds [221]. The interaction of mercury compounds suggests the production of oxidative damage through the accumulation of reactive oxygen species (ROS) which would normally be eliminated by cellular antioxidants (reference). Hw does Hg cause cancer ENVIRONMENTAL REGULATION AND CONTROL OF HEAVY METAL POLLUTION CHAPTER THREE Conclusion A comprehensive analysis of published data indicates that heavy metals such as arsenic cadmium, chromium, lead, and mercury, occur naturally. However, anthropogenic activities contribute significantly to environmental contamination. These metals are systemic toxicants known to induce adverse health effects in humans, including cardiovascular diseases, developmental abnormalities, neurologic and neurobehavioral disorders, diabetes, hearing loss, hematologic and immunologic disorders, and various types of cancer. The main pathways of exposure include ingestion, inhalation, and dermal contact. The severity of adverse health effects is related to the type of heavy metal and its chemical form, and is also time- and dose-dependent. Among many other factors, speciation plays a key role in metal toxicokinetics and toxicodynamics, and is highly influenced by factors such as valence state, particle size, solubility, biotransformation, and chemical form. Several studies have shown that toxic metals exposure causes long term health problems in human populations. Although the acute and chronic effects are known for some metals, little is known about the health impact of mixtures of toxic elements. Recent reports have pointed out that these toxic elements may interfere metabolically with nutritionally essential metals such as iron, calcium, copper, and zinc [245, 246]. In many areas of metal pollution, chronic low dose exposure to multiple elements is a major public health concern. Elucidating the mechanistic basis of heavy metal interactions is essential for health risk assessment and management of chemical mixtures. Hence, research is needed to further elucidate the molecular mechanisms and public health impact associated with human exposure to mixtures of toxic metals. RECOMMEDATION REFERENCES 1. Fergusson JE, editor. The Heavy Elements: Chemistry, Environmental Impact and Health Effects. Oxford: Pergamon Press; 1990. 2. Duffus JH. Heavy metals-a meaningless term? Pure Appl Chem. 2002;74(5):793–807. 3. Bradl H, editor. Heavy Metals in the Environment: Origin, Interaction and Remediation Volume 6. London: Academic Press; 2002. 4. He ZL, Yang XE, Stoffella PJ. Trace elements in agroecosystems and impacts on the environment. J Trace Elem Med Biol. 2005;19(2–3):125–140. [PubMed] 5. Goyer RA. Toxic effects of metals. In: Klaassen CD, editor. Cassarett and Doull’s Toxicology: The Basic Science of Poisons. New York: McGraw-Hill Publisher; 2001. pp. 811–867. 6. Herawati N, Suzuki S, Hayashi K, Rivai IF, Koyoma H. Cadmium, copper and zinc levels in rice and soil of Japan, Indonesia and China by soil type. Bull Env Contam Toxicol. 2000;64:33–39. [PubMed] 7. Shallari S, Schwartz C, Hasko A, Morel JL. Heavy metals in soils and plants of serpentine and industrial sites of Albania. Sci Total Environ. 1998;19209:133–142. [PubMed] 8. Nriagu JO. A global assessment of natural sources of atmospheric trace metals.Nature. 1989;338:47–49. 9. Arruti A, Fernández-Olmo I, Irabien A. Evaluation of the contribution of local sources to trace metals levels in urban PM2.5 and PM10 in the Cantabria region (Northern Spain) J Environ Monit. 2010;12(7):1451–1458. [PubMed] 10. Sträter E, Westbeld A, Klemm O. Pollution in coastal fog at Alto Patache, Northern Chile. Environ Sci Pollut Res Int. 2010 [Epub ahead of print] [PubMed] 11. Pacyna JM. Monitoring and assessment of metal contaminants in the air. In: Chang LW, Magos L, Suzuli T, editors. Toxicology of Metals. Boca Raton, FL: CRC Press; 1996. pp. 9–28. 12. WHO/FAO/IAEA. World Health Organization. Switzerland: Geneva; 1996. Trace Elements in Human Nutrition and Health. 13. Kabata- Pendia A 3rd, editor. Trace Elements in Soils and Plants. Boca Raton, FL: CRC Press; 2001. 14. Hamelink JL, Landrum PF, Harold BL, William BH, editors. Bioavailability: Physical, Chemical, and Biological Interactions. Boca Raton, FL: CRC Press Inc; 1994. 15. Verkleji JAS. In: The effects of heavy metals stress on higher plants and their use as biomonitors In Plant as Bioindicators: Indicators of Heavy Metals in the Terrestrial Environment. Markert B, editor. New York: VCH; 1993. pp. 415–424. 16. Stern BR. Essentiality and toxicity in copper health risk assessment: overview, update and regulatory considerations. Toxicol Environ Health A. 2010;73(2):114–127. [PubMed] 17. Harvey LJ, McArdle HJ. Biomarkers of copper status: a brief update. Br J Nutr. 2008;99(S3):S10–S13. [PubMed] 18. Agency for Toxic Substances and Disease Registry (ATSDR) Toxicological Profile for Copper. Atlanta, GA: Centers for Disease Control; 2002. 19. Tchounwou P, Newsome C, Williams J, Glass K. Copper-induced cytotoxicity and transcriptional activation of stress genes in human liver carcinoma cells. Metal Ions Biol Med. 2008;10:285–290. [PMC free article] [PubMed] 20. Chang LW, Magos L, Suzuki T, editors. Toxicology of Metals. Boca Raton. FL, USA: CRC Press; 1996. 21. Wang S, Shi X. Molecular mechanisms of metal toxicity and carcinogenesis. Mol Cell Biochem. 2001;222:3–9. [PubMed] 22. Beyersmann D, Hartwig A. Carcinogenic metal compounds: recent insight into molecular and cellular mechanisms. Arch Toxicol. 2008;82(8):493–512. [PubMed] 23. Yedjou CG, Tchounwou PB. Oxidative stress in human leukemia cells (HL-60), human liver carcinoma cells (HepG2) and human Jerkat-T cells exposed to arsenic trioxide. Metal Ions Biol Med. 2006;9:298–303. [PMC free article] [PubMed] 24. Yedjou GC, Tchounwou PB. In vitro cytotoxic and genotoxic effects of arsenic trioxide on human leukemia cells using the MTT and alkaline single cell gel electrophoresis (comet) assays. Mol Cell Biochem. 2007;301:123–130. [PMC free article] [PubMed] 25. Tchounwou PB, Centeno JA, Patlolla AK. Arsenic toxicity, mutagenesis and carcinogenesis - a health risk assessment and management approach. Mol Cell Biochem. 2004;255:47–55. [PubMed] 26. Tchounwou PB, Ishaque A, Schneider J. Cytotoxicity and transcriptional activation of stress genes in human liver carcinoma cells (HepG2) exposed to cadmium chloride. Mol Cell Biochem. 2001;222:21–28. [PubMed] 27. Patlolla A, Barnes C, Field J, Hackett D, Tchounwou PB. Potassium dichromate-induced cytotoxicity, genotoxicity and oxidative stress in human liver carcinoma (HepG2) cells. Int J Environ Res Public Health. 2009;6:643–653. [PMC free article] [PubMed] 28. Patlolla A, Barnes C, Yedjou C, Velma V, Tchounwou PB. Oxidative stress, DNA damage and antioxidant enzyme activity induced by hexavalent chromium in Sprague Dawley rats. Environ Toxicol. 2009;24(1):66–73. [PMC free article] [PubMed] 29. Yedjou GC, Tchounwou PB. N-acetyl-cysteine affords protection against lead-induced cytotoxicity and oxidative stress in human liver carcinoma (HepG2) cells. Intl J Environ Res Public Health. 2008;4(2):132–137. [PMC free article] [PubMed] 30. Tchounwou PB, Yedjou CG, Foxx D, Ishaque A, Shen E. Lead-induced cytotoxicity and transcriptional activation of stress genes in human liver carcinoma cells (HepG2) Mol Cell Biochem. 2004;255:161–170. [PubMed] 31. Sutton DJ, Tchounwou PB. Mercury induces the externalization of phosphatidylserine in human proximal tubule (HK-2) cells. Intl J Environ Res Public Health. 2007;4(2):138–144. [PMC free article] [PubMed] 32. Sutton D, Tchounwou PB, Ninashvili N, Shen E. Mercury induces cytotoxicity, and transcriptionally activates stress genes in human liver carcinoma cells. Intl J Mol Sci. 2002;3(9):965–984. 33. Agency for Toxic Substances and Disease Registry (ATSDR) Toxicological Profile for Arsenic TP-92/09. Georgia: Center for Disease Control, Atlanta; 2000. 34. Tchounwou PB, Wilson B, Ishaque A. Important considerations in the development of public health advisories for arsenic and arsenic-containing compounds in drinking water. Rev Environ Health. 1999;14(4):211–229. [PubMed] 35. Centeno JA, Tchounwou PB, Patlolla AK, Mullick FG, Murakat L, Meza E, Gibb H, Longfellow D, Yedjou CG. Environmental pathology and health effects of arsenic poisoning: a critical review. In: Naidu R, Smith E, Smith J, Bhattacharya P, editors. Managing Arsenic In the Environment: From Soil to Human Health. Adelaide, Australia: CSIRO Publishing Corp.; 2005. 36. Rousselot P, Laboume S, Marolleau JP, Larghero T, Noguera ML, Brouet JC, Fermand JP. Arsenic trioxide and melarsoprol induce apoptosis in plasma cell lines and in plasma cells from myeloma patients. Cancer Res. 1999;59:1041–1048. [PubMed] 37. National Research Council Canada (NRCC) Effects of Arsenic in the Environment. National Research Council of Canada; 1978. pp. 1–349. 38. Morton WE, Dunnette DA. Health effects of environmental arsenic. In: Nriagu JO, editor. Arsenic in the Environment Part II: Human Health and Ecosystem Effects. New York: John Wiley & Sons, Inc; 1994. pp. 17–34. 39. National Research Council. Arsenic in Drinking Water. 2001 Update. 2001 On line at: http://www.nap.edu/ books/0309076293/html/ [PubMed] 40. Tchounwou PB, Centeno JA. Toxicologic pathology. In: Gad SC, editor. Handbook of Pre-Clinical Development. New York. NY: John Wiley & Sons; 2008. pp. 551–580. 41. Tchounwou PB, Patlolla AK, Centeno JA. Carcinogenic and systemic health effects associated with arsenic exposure-a critical review. Toxicol Pathol. 2003;31(6):575–588. [PubMed] 42. Tchounwou PB, Wilson BA, Abdelgnani AA, Ishaque AB, Patlolla AK. Differential cytotoxicity and gene expression in human liver carcinoma (HepG2) cells exposed to arsenic trioxide and monosodium acid methanearsonate (MSMA) Intl J Mol Sci. 2002;3:1117–1132. 43. Yedjou GC, Moore P, Tchounwou PB. Dose and time dependent response of human leukemia (HL-60) cells to arsenic trioxide. Intl J Environ Res Public Health. 2006;3(2):136–140. [PMC free article] [PubMed] 44. Chappell W, Beck B, Brown K, North D, Thornton I, Chaney R, Cothern R, Cothern CR, North DW, Irgolic K, Thornton I, Tsongas T. Inorganic arsenic: A need and an opportunity to improve risk assessment. Environ Health Perspect. 1997;105:1060–1067. [PMC free article] [PubMed] 45. Centeno JA, Gray MA, Mullick FG, Tchounwou PB, Tseng C. Arsenic in drinking water and health issues. In: Moore TA, Black A, Centeno JA, Harding JS, Trumm DA, editors. Metal Contaminants in New Zealand. New Zealand: Resolutionz Press; 2005. pp. 195–219. 46. Abernathy CO, Liu YP, Longfellow D, Aposhian HV, Beck B, Fowler B, Goyer R, Menzer R, Rossman T, Thompson C, Waalkes R. Arsenic: health effects, mechanisms of actions and research issues. Environ Health Perspect. 1999;107:593–597. [PMC free article] [PubMed] 47. Hughes MF. Arsenic toxicity and potential mechanisms of action. Toxicol Lett. 2002;133:1–16. [PubMed] 48. Wang Z, Rossman TG. In: The Toxicology of Metals. Cheng LW, editor. Vol. 1. Boca Raton, FL: CRC Press; 1996. pp. 221–243. 49. Belton JC, Benson NC, Hanna ML, Taylor RT. Growth inhibition and cytotoxic effects of three arsenic compounds on cultured Chinese hamster ovary cells. J Environ Sci Health. 1985;20A:37–72. 50. Li JH, Rossman TC. Inhibition of DNA ligase activity by arsenite: A possible mechanism of its comutagenesis. Mol Toxicol. 1989;2:1–9. [PubMed] 51. Jha AN, Noditi M, Nilsson R, Natarajan AT. Genotoxic effects of sodium arsenite on human cells. Mutat Res. 1992;284:215–221. [PubMed] 52. Hartmann A, Speit G. Comparative investigations of the genotoxic effects of metals in the single cell gel assay and the sister-chromatid exchange test. Environ Mol Mutagen. 1994;23:299–305. [PubMed] 53. Patlolla A, Tchounwou PB. Cytogenetic evaluation of arsenic trioxide toxicity in Sprague-Dawley rats. Mut Res – Gen Tox Environ Mutagen. 2005;587(1–2):126–133. [PubMed] 54. Basu A, Mahata J, Gupta S, Giri AK. Genetic toxicology of a paradoxical human carcinogen, arsenic: a review. Mutat Res. 2001;488:171–194. [PubMed] 55. Landolph JR. Molecular and cellular mechanisms of transformation of C3H/10T1/2C18 and diploid human fibroblasts by unique carcinogenic, non- mutagenic metal compounds.A review. Biol Trace Elem Res. 1989;21:459–467. [PubMed] 56. Takahashi M, Barrett JC, Tsutsui T. Transformation by inorganic arsenic compounds of normal Syrian hamster embryo cells into a neoplastic state in which they become anchorage-independent and cause tumors in newborn hamsters. Int J Cancer. 2002;99:629–634. [PubMed] 57. Anderson D, Yu TW, Phillips BJ, Schemezer P. The effect of various antioxidants and other modifying agents on oxygen-radical-generated DNA damage in human lymphocytes in the Comet assay. Mutation Res. 1994;307:261–271. [PubMed] 58. Saleha Banu B, Danadevi K, Kaiser Jamil, Ahuja YR, Visweswara Rao K, Ishap M. In vivo genotoxic effect of arsenic trioxide in mice using comet assay.Toxicol. 2001;162:171–177. [PubMed] 59. Hartmann A, Peit G. Comparative investigations of the genotoxic effects of metals in the single cell gel assay and the sister chromatid exchange test. Environ Mol Mutagen. 1994;23:299–305. [PubMed] 60. Barrett JC, Lamb PW, Wang TC, Lee TC. Mechanisms of arsenic-induced cell transformation. Biol. Trace Ele Res. 1989;21:421–429. [PubMed] 61. Tchounwou PB, Yedjou CG, Dorsey WC. Arsenic trioxide - induced transcriptional activation and expression of stress genes in human liver carcinoma cells (HepG2) Cell Mol Biol. 2003;49:1071–1079. [PubMed] 62. Zhao CQ, Young MR, Diwan BA, Coogan TP, Waalkes MP. Association of arsenic-induced malignant transformation with DNA hypomethylation and aberrant gene expression. Proc Natl Acad Sci USA. 1997;94:10907–10912. [PMC free article] [PubMed] 63. Liu Y, Guyton KZ, Gorospe M, Xu Q, Lee JC, Holbrook NJ. Differential activation of ERK, JNK/SAPK and P38/CSBP/RK map kinase family members during the cellular response to arsenite. Free Rad Biol Med. 1996;21:771–781. [PubMed] 64. Ludwig S, Hoffmeyer A, Goebeler M, Kilian K, Hafner H, Neufeld B, Han J, Rapp UR. The stress inducer arsenite activates mitogen-activated protein kinases extracellular signal-regulated kinases 1 and 2 via a MAPK kinase 6/p38- dependent pathway. J Biol Chem. 1998;273:1917–1922. [PubMed] 65. Trouba KJ, Wauson EM, Vorce RL. Sodium arsenite-induced dysregulation of proteins involved in proliferative signaling. Toxicol Appl Pharmacol. 2000;164(2):161–170. [PubMed] 66. Vogt BL, Rossman TG.Effects of arsenite on p53, p21 and cyclin D expression in normal human fibroblasts- a possible mechanism for arsenite’s comutagenicity. Mutat Res. 2001;478(1–2):159–168. [PubMed] 67. Chen NY, Ma WY, Huang C, Ding M, Dong Z. Activation of PKC is required for arsenite-induced signal transduction. J Environ Pathol Toxicol Oncol. 2000;19(3):297–306. [PubMed] 68. Porter AC, Fanger GR, Vaillancourt RR. Signal tansduction pathways regulated by arsenate and arsenite. Oncogene. 1999;18(54):7794–7802. [PubMed] 69. Soignet SL, Frankel SR, Douer D, Tallman MS, Kantarjian H, Calleja E, Stone RM, Kalaycio M, Scheinberg DA, Steinherz P, Sievers EL, Coutré S, Dahlberg S, Ellison R, Warrell RP., Jr United States multicenter study of arsenic trioxide in relapsed acute promyelocytic leukemia. J Clin Oncol. 2001;19(18):3852–3860. [PubMed] 70. Murgo AJ. Clinical trials of arsenic trioxide in hematologic and solid tumors: overview of the National Cancer Institute Cooperative Research and Development Studies. Oncologist. 2001;6(2):22–28. [PubMed] 71. Puccetti ES, Guller S, Orleth A, Bruggenolte N, Hoelzer D, Ottmann OG, Ruthardt M. BCR-ABL mediates arsenic trioxide-induced apoptosis independently of its aberrant kinase activity. Cancer Res. 2000;60(13):3409–3413. [PubMed] 72. Seol JG, Park WH, Kim ES, Jung CW, Hyun JM, Kim BK, Lee YY. Effect of arsenic trioxide on cell cycle arrest in head and neck cancer cell-line PCI-1.Biochem Biophys Res Commun. 1999;265(2):400–404. [PubMed] 73. Alemany M, Levin J. The effects of arsenic trioxide on human Megakaryocytic leukemia cell lines with a comparison of its effects on other cell lineages. Leukemia Lymphoma. 2000;38(1–2):153–163. [PubMed] 74. Deaglio S, Canella D, Baj G, Arnulfo A, Waxman S, Malavasi F. Evidence of an immunologic mechanism behind the therapeutic effects of arsenic trioxide on myeloma cells. Leuk Res. 2001;25(3):237–239. [PubMed] 75. Tully DB, Collins BJ, Overstreet JD, Smith CS, Dinse GE, Mumtaz MM, Chapin RE. Effects of arsenic, cadmium, chromium and lead on gene expression regulated by a battery of 13 different promoters in recombinant HepG2 cells. Toxicol Appl Pharmacol. 2000;168(2):79–90. [PubMed] 76. Lu T, Liu J, LeCluyse EL, Zhou YS, Cheng ML, Waalkes MP. Application of cDNA microarray to the study of arsenic-induced liver diseases in the population of Guizhou, China. Toxicol Sci. 2001;59(1):185–192. [PubMed] 77. Harris CC. Chemical and physical carcinogenesis: advances and perspectives. Cancer Res. 1991;51:5023s–5044s. [PubMed] 78. Graham-Evans B, Colhy HHP, Yu H, Tchounwou PB. Arsenic-induced genotoxic and cytotoxic effects in human keratinocytes, melanocytes, and dendritic cells. Intl J Environ Res Public Health. 2004;1(2):83–89. [PubMed] 79. Stevens JJ, Graham B, Walker AM, Tchounwou PB, Rogers C. The effects of arsenic trioxide on DNA synthesis and genotoxicity in human colon cancer cells. Intl J Environ Res Public Health. 2010;7(5):2018–2032. [PMC free article] [PubMed] 80. Walker AM, Stevens JJ, Ndebele K, Tchounwou PB. Arsenic trioxide modulates DNA synthesis and apoptosis in lung carcinoma cells. Intl J Environ Res Public Health. 2010;7(5):1996–2007. [PMC free article] [PubMed] 81. Yedjou CG, Tchounwou PB. Modulation of p53, c-fos, RARE, cyclin A and cyclin D1 expression in human leukemia (HL-60) cells exposed to arsenic trioxide.Mol Cell Biochem. 2009;331:207–214. [PMC free article] [PubMed] 82. Yedjou C, Sutton LM, Tchounwou PB. Genotoxic mechanisms of arsenic trioxide effect in human Jurkat T-lymphoma cells. Metal Ions Biol Med. 2008;10:495–499. [PMC free article] [PubMed] 83. Brown E, Yedjou C, Tchounwou PB. Cytotoxicty and oxidative stress in human liver carcinoma cells exposed to arsenic trioxide. Metal Ions Biol Med. 2008;10:583–587. [PMC free article] [PubMed] 84. Yedjou CG, Thuisseu L, Tchounwou C, Gomes M, Howard C, Tchounwou PB. Ascorbic acid potentiation of arsenic trioxide anticancer activity against acute promyelocytic leukemia. Arch Drug Inf. 2009;2(4):59–65. [PMC free article] [PubMed] 85. Yedjou C, Rogers C, Brown E, Tchounwou P. Differential effect of ascorbic acid and n-acetyl-cysteine on arsenic trioxide - mediated oxidative stress in human leukemia (HL-60) cells. J Biochem Mol Tox. 2008;22:85–92. [PMC free article] [PubMed] 86. Yedjou GC, Moore P, Tchounwou PB. Dose- and time-dependent response of human leukemia (HL-60) cells to arsenic tic trioxide treatment. Intl J Environ Res Public Health. 2006;3(2):136–140. [PMC free article] [PubMed] 87. Miller WH, Schipper HM, Lee JS, Singer J, Waxman S. Mechanisms of action of arsenic trioxide - review. Cancer Res. 2002;62:3893–3903. [PubMed] 88. Gesamp. IMO/FAO/UNESCO/WMO/WHO/IAEA/UN/UNEP Joint Group of Experts on the Scientific Aspects of Marine Pollution: Report of the seventeenth session. Geneva, Switzerland: World Health Organization; 1987. (Reports and Studies No. 31) 89. Wilson DN. Association Cadmium. Cadmium - market trends and influences; London.Cadmium 87 Proceedings of the 6th International Cadmium Conference; 1988. pp. 9–16. 90. U.S Environmental Protection Agency (EPA) [accessed 4 March 2009];Cadmium Compounds. 2006 91. International Agency for Research on Cancer (IARC) Monographs – Cadmium. Lyon, France: 1993. 92. Paschal DC, Burt V, Caudill SP, Gunter EW, Pirkle JL, Sampson EJ, et al. Exposure of the U.S. population aged 6 years and older to cadmium: 1988–1994. Arch Environ Contam Toxicol. 2000;38:377–383. [PubMed] 93. Agency for Toxic Substances and Disease Registry (ATSDR) Draft Toxicological Profile for Cadmium. Atlanta, GA: 2008. 94. Satarug S, Baker JR, Urbenjapol S, Haswell-Elkins M, Reilly PE, Williams DJ, et al. A global perspective on cadmium pollution and toxicity in non-occupationally exposed population. Toxicol Lett. 2003;137:65–83. [PubMed] 95. Davison AG, Fayers PM, Taylor AJ, Venables KM, Darbyshire J, Pickering CA, et al. Cadmium fume inhalation and emphysema. Lancet. 1988;1(8587):663–667. [PubMed] 96. Mascagni P, Consonni D, Bregante G, Chiappino G, Toffoletto F. Olfactory function in workers exposed to moderate airborne cadmium levels. Neurotoxicol. 2003;24:717–724. [PubMed] 97. Åkesson A, Bjellerup P, Lundh T, Lidfeldt J, Nerbrand C, Samsioe G, et al. Cadmium-induced effects on bone in a population-based study of women. Environ Health Perspect. 2006;114:830–834. [PMC free article] [PubMed] 98. Gallagher CM, Kovach JS, Meliker JR. Urinary cadmium and osteoporosis in U.S. women ≥ 50 years of age: NHANES 1988–1994 and 1999–2004. Environ Health Perspect. 2008;116:1338–1343. [PMC free article] [PubMed] 99. Schutte R, Nawrot TS, Richart T, Thijs L, Vanderschueren D, Kuznetsova T, et al. Bone resorption and environmental exposure to cadmium in women: a population study. Environ Health Perspect. 2008;116:777–783. [PMC free article] [PubMed] 100. Jarup L, Berglund M, Elinder CG, et al. Health effects of cadmium exposure--a review of the literature and a risk estimate [published erratum appears in Scand J Work Environ Health 1998 Jun; 24(3):240] Scand J Work Environ Health. 1998;24(1):1. [PubMed] 101. Wittman R, Hu H. Cadmium exposure and nephropathy in a 28-year-old female metals worker. Environ Health Perspect. 2002;110:1261. [PMC free article] [PubMed] 102. Becker K, Kaus S, Krause C, Lepom P, Schulz C, Seiwert M, et al. German Environmental Survey 1998 (GerES III): environmental pollutants in blood of the German population. Intl J Hyg Environ Health. 2002;205:297–308. [PubMed] 103. Mannino DM, Holguin F, Greves HM, Savage-Brown A, Stock AL, Jones RL. Urinary cadmium levels predict lower lung function in current and former smokers: data from the Third National Health and Nutrition Examination Survey. Thorax. 2004;59:194–198. [PMC free article] [PubMed] 104. Elinder CG, Järup L. Cadmium exposure and health risks: Recent findings. Ambio. 1996;25:370. 105. Baselt RC, Cravey RH. Disposition of Toxic Drugs and Chemicals in Man. 4th Edn. Chicago, IL: Year Book Medical Publishers; 1995. pp. 105–107. 106. Baselt RC. Disposition of Toxic Drugs and Chemicals in Man. 5th Ed. Foster City, CA: Chemical Toxicology Institute; 2000. 107. Singhal RL, Merali Z, Hrdina PD. Aspects of the biochemical toxicology of cadmium. Fed Proc. 1976;35(1):75–80. [PubMed] 108. Waalkes MP, Berthan G, editors. Handbook on Metal-Ligand Interactions of Biological Fluids.Vol. 2. New York: Marcel Dekker; 1995. pp. 471–482. 109. Waalkes MP, Misra RR, Chang LW, editors. Toxicology of Metals. Boca Raton, FL: CRC Press; 1996. pp. 231–244. 110. Waalkes MP, Rehm S. Fundam Appl Toxicol. 1992;19:512. [PubMed] 111. Stohs Bagchi. Oxidative mechanisms in the toxicity of metal ions. Free Radic Biol Med. 1995;18:321–336. [PubMed] 112. Mitra RS. Protein synthesis in Escherichia coli during recovery from exposure to low levels of Cd2+ Appl Environ Microbiol. 1984;47:1012–1016. [PMC free article] [PubMed] 113. Blom A, Harder W, Matin A. Unique and overlapping pollutant stress proteins of Escherichia coli. Appl Environ Microbiol. 1992;58:331–334. [PMC free article] [PubMed] 114. Feriance PA, Farewell Nystrom T. The cadmium-stress stimulon of Escherichia coli K-12.Microbiol. 1998;144:1045–1050. [PubMed] 115. Coogan TP, Bare RM, Waalkes MP. Cadmium-induced DNA strand damage in cultured liver cells: reduction in cadmium genotoxicity following zinc pretreatment. Toxicol Appl Pharmacol. 1992;113:227–233. [PubMed] 116. Tsuzuki K, Sugiyama M, Haramaki N. DNA single-strand breaks and cytotoxicity induced by chromate (VI), cadmium (II), and mercury (II) in hydrogen peroxide-resistant cell lines. Environ Health Perspect. 1994;102:341–342. [PMC free article] [PubMed] 117. Mukherjee S, Das SK, Kabiru W, Russell KR, Greaves K, Ademoyero AA, et al. Acute cadmium toxicity and male reproduction. Adv Reprod. 2002;6:143–155. 118. Rossman TG, Roy NK, Lin WC. Is cadmium genotoxic? IARC Sci Publ. 1992;118:367–375. [PubMed] 119. Smith JB, Dwyer SC, Smith L. Lowering extracellular pH evokes inositol polyphosphate formation and calcium mobilization. J Biol Chem. 1989;264:8723–8728. [PubMed] 120. Th'evenod F, Jones SW. Cadmium block of calcium current in frog sympathetic neurons. Biophys J. 1992;63:162–168. [PMC free article] [PubMed] 121. Suszkiw J, Toth G, Murawsky M, Cooper GP. Effects of Pb2+ and Cd2+ on acetylcholine release and Ca2+ movements in synaptosomes and subcellular fractions from rat brain and Torpedo electric organ. Brain Res. 1984;323:31–46. [PubMed] 122. Dally H, Hartwig A. Induction and repair inhibition of oxidative DNA damage by nickel (II) and cadmium (II) in mammalian cells. Carcinogenesis. 1997;18:1021–1026. [PubMed] 123. Abshire MK, Devor DE, Diwan BA, Shaughnessy JD, Jr, Waalkes MP. In vitro exposure to cadmium in rat L6 myoblasts can result in both enhancement and suppression of malignant progression in vivo. Carcinogenesis. 1996;17:1349–1356. [PubMed] 124. Durnam DM, Palmiter RD. Transcriptional regulation of the mouse metallothionein-I gene by heavy metals. J Biol Chem. 1981;256:5712–5716. [PubMed] 125. Hwua Y, Yang J. Effect of 3-aminotriazole on anchorage independence and mutagenicity in cadmium- and lead-treated diploid human fibroblasts. Carcinogenesis. 1998;19:881–888. [PubMed] 126. Landolph J. Molecular mechanisms of transformation of CH3/10T1/2 C1 8 mouse embryo cells and diploid human fibroblasts by carcinogenic metal compounds. Environ Health Perspect. 1994;102:119–125. [PMC free article] [PubMed] 127. Nishijo M, Tawara K, Honda R, Nakagawa H, Tanebe K, Saito S. Relationship between newborn size and mother's blood cadmium levels, Toyama, Japan. Arch Environ Health. 2004;59(1):22–25. [PubMed] 128. Zhang YL, Zhao YC, Wang JX, Zhu HD, Liu QF, Fan YG, et al. Effect of environmental exposure to cadmium on pregnancy outcome and fetal growth: a study on healthy pregnant women in China. J Environ Sci Health B. 2004;39:2507–2515. [PubMed] 129. Jacobs JA, Testa SM. Overview of chromium(VI) in the environment: background and history. In: Guertin J, Jacobs JA, Avakian CP, editors. Chromium (VI) Handbook. Boca Raton, Fl: CRC Press; 2005. pp. 1–22. 130. Agency for Toxic Substances and Disease Registry (ATSDR) Toxicological Profile for Chromium. Atlanta, GA: U.S. Department of Health and Human Services, Public Health Service; 131. IARC. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans Vol. 49. Lyon, France: IARC Scientific Publications, IARC; 1990. Chromium, nickel and welding. 132. U.S. EPA. Environmental Criteria and Assessment Office. Cincinnati, OH: United States Environmental Protection Agency; 1992. Integrated Risk Information System (IRIS) 133. Velma V, Vutukuru SS, Tchounwou PB. Ecotoxicology of hexavalent chromium in freshwater fish: a critical review. Rev Environ Health. 2009;24(2):129–145. [PMC free article] [PubMed] 134. Cohen MD, Kargacin B, Klein CB, Costa M. Mechanisms of chromium carcinogenicity and toxicity. Crit Rev Toxicol. 1993;23:255–281. [PubMed] 135. Norseth T. The carcinogenicity of chromium. Environ Health Perspect. 1981;40:121–130. [PMC free article] [PubMed] 136. Wang XF, Xing ML, Shen Y, Zhu X, Xu LH.Oral administration of Cr (VI) induced oxidative stress, DNA damage and apoptotic cell death in mice.Toxicology. 2006;228:16–23. [PubMed] 137. Guertin J. Toxicity and health effects of chromium (all oxidation states) In: Guertin J, Jacobs JA, Avakian CP, editors. Chromium (VI) Handbook. Boca Raton, FL: CRC Press; 2005. pp. 216–234. 138. Occupational Safety and Health Administration (OSHA) Federal Register. Vol. 71. Washington, DC: Final rule; 2006. Occupational exposure to hexavalent chromium; pp. 10099–10385. [PubMed] 139. Singh J, Pritchard DE, Carlisle DL, Mclean JA, Montaser A, Orenstein JM, Patierno SR. Internalization of carcinogenic lead chromate particles by cultured normal human lung epithelial cells: Formation of intracellular lead-inclusion bodies and induction of apoptosis. Toxicol Appl Pharmacol. 1999;161:240–248. [PubMed] 140. Langård S, Vigander T. Occurrence of lung cancer in workers producing chromium pigments. Br J Ind Med. 1983;40(1):71–74. [PMC free article] [PubMed] 141. Agency for Toxic Substances and Disease Registry (ATSDR) U.S. Department of Health and Human Services. Atlanta, GA: Public Health Service; 2008. Toxicological Profile for Chromium. 142. Costa M. Toxicity and carcinogenicity of Cr(VI) in animal models and humans. Critical Reviews in Toxicology. 1997;27:431–442. [PubMed] 143. Shelnutt SR, Goad P, Belsito DV. Dermatological toxicity of hexavalent chromium. Crit. Rev Toxicol. 2007;37:375–387. [PubMed] 144. WHO/IPCS. World Health Organization. Geneva, Switzerland: 1988. Environmental Health Criteria 61: Chromium. 145. Chen TL, Wise SS, Kraus S, Shaffiey F, Levine K, Thompson DW, Romano T, O’Hara T, Wise JP. Particulate hexavalent chromium is cytotoxic and genotoxic to the North Atlantic right whale (Eubalaena glacialis) lung and skin fibroblasts. Environ Mol Mutagenesis. 2009;50:387–393. [PubMed] 146. Connett PH, Wetterhahn KE. Metabolism of carcinogenic chromate by cellular constituents. Struct Bonding. 1983;54:93–24. 147. De Flora S, Bagnasco M, Serra D, Zanacchi P. Genotoxicity of chromium compounds: a review. Mutat Res. 1990;238:99–172. [PubMed] 148. Dayan AD, Paine AJ. Mechanisms of chromium toxicity, carcinogenicity and allergenicity: review of the literature from 1985 to 2000. Hum Exp Toxicol. 2001;20(9):439–451. [PubMed] 149. De Mattia G, Bravi MC, Laurenti O, De Luca O, Palmeri A, Sabatucci A, Mendico G, Ghiselli A. Impairment of cell and plasma redox state in subjects professionally exposed to chromium. Am J Ind Med. 2004;46(2):120–125. [PubMed] 150. O’ Brien TJ, Ceryak S, Patierno SR. Complexities of chromium carcinogenesis: role of cellular response, repair and recovery mechanisms. Mutat Res. 2003;533:3–36. [PubMed] 151. Kim E, Na KJ. Nephrotoxicity of sodium dichromate depending on the route of administration.Arch Toxicol. 1991;65:537–541. [PubMed] 152. Gumbleton M, Nicholls PJ. Dose-response and time-response biochemical and histological study of potassium dichromate-induced nephrotoxicity in the rat.Food Chem Toxicol. 1988;26:37–44. [PubMed] 153. Bagchi D, Hassoun EA, Bagchi M, Muldoon D, Stohs SJ. Oxidative stress induced by chronic administration of sodium dichromate (Cr VI) to rats. Comp Biochem Physiol. 1995;1995;110C:281–287. [PubMed] 154. Bagchi D, Vuchetich PJ, Bagchi M, Hassoun EA, Tran MX, Tang L, Stohs SJ. Induction of oxidative stress by chronic administration of sodium dichromate (chromium VI) and cadmium chloride (cadmium II) to rats. Free Rad Biol Med. 1997;22:471–478. [PubMed] 155. Gambelunghe A, Piccinini R, Ambrogi M, Villarini M, Moretti M, Marchetti C, Abbritti G, Muzi G. Primary DNA damage in chrome-plating workers. Toxicology. 2003;188(2–3):187–195. [PubMed] 156. Goulart M, Batoreu MC, Rodrigues AS, Laires A, Rueff J. Lipoperoxidation products and thiol antioxidants in chromium-exposed workers. Mutagenesis. 2005;20(5):311–315. [PubMed] 157. Wise JP, Wise SS, Little JE. The cytotoxicity and genotoxicity of particulate and soluble hexavalent chromium in human lung cells. Mutat Res. 2002;517:221–229. [PubMed] 158. Wise SS, Holmes AL, Ketterer ME, Hartsock WJ, Fomchenko E, Katsifis SP, Thompson WD, Wise JP. Chromium is the proximate clastogenic species for lead chromate-induced clastogenicity in human bronchial cells. Mutat Res. 2004;560:79–89. [PubMed] 159. Xie H, Wise SS, Holmes AL, Xu B, Wakeman T, Pelsue SC, Singh NP, Wise JP. Carcinogenic lead chromate induces DNA double-strand breaks in human lung cells. Mutat Res. 2005;586:160–172. [PMC free article] [PubMed] 160. Zhitkovich A, Song Y, Quievryn G, Voitkun V. Non-oxidative mechanisms are responsible for the induction of mutagenesis by reduction of Cr(VI) with cysteine: role of ternary DNA adducts in Cr(III)-dependent mutagenesis. Biochem. 2001;40(2):549–60. [PubMed] 161. Katz SA, Salem H. The toxicology of chromium with respect to its chemical speciation: a review. J Appl Toxicol. 1993;13(3):217–224. [PubMed] 162. Patlolla AK, Armstrong N, Tchounwou PB. Cytogenetic evaluation of potassium dichromate toxicity in bone marrow cells of Sprague-Dawley rats. Metal Ions Biol Med. 2008;10:353–358. 163. Velma V, Tchounwou PB. Chromium-induced biochemical, genotoxic and histopathologic effects in liver and kidney of goldfish, carassius auratus. Mutat Res. 2010;698(1–2):43–51. [PMC free article] [PubMed] 164. Norseth T. The carcinogenicity of chromium and its salts. Br J Ind Med. 1986;3(10):649–651. [PMC free article] [PubMed] 165. Gabby PN. Lead: in Mineral Commodity Summaries. Reston, VA: U.S. Geological Survey; 2006. available at http://minerals.usgs.gov/minerals/pubs/commodity/lead/lead_mcs05.pdf. 166. Gabby PN. “Lead.”Environmental Defense “Alternatives to Lead-Acid Starter Batteries,” Pollution Prevention Fact Sheet.2003 available at http://www.cleancarcampaign.org/FactSheet_BatteryAlts.pdf. 167. Centers for Disease control (CDC) Preventing Lead Poisoning in Young children: A statement by the Centers for Disease Control. Atlanta, GA: 1991. 168. Jacobs DE, Clickner RP, Zhou JY, et al. The prevalence of lead-based paint hazards in U.S. housing. Environ Health Perspect. 2002;110:A599–A606. [PMC free article] [PubMed] 169. Farfel MR, Chisolm JJ., Jr An evaluation of experimental practices for abatement of residential lead-based paint: report on a pilot project. Environ Res. 1991;55:199–212. [PubMed] 170. Centers for Disease Control and Prevention CDC) Managing Elevated Blood Lead Levels Among Young Children: Recommendations From the Advisory Committee on Childhood Lead Poisoning Prevention. Atlanta: 2001. 171. Lanphear BP, Matte TD, Rogers J, et al. The contribution of lead-contaminated house dust and residential soil to children's blood lead levels. A pooled analysis of 12 epidemiologic studies. Environ Res. 1998;79:51–68. [PubMed] 172. Charney E, Sayre J, Coulter M. Increased lead absorption in inner city children: where does the lead come from? Pediatrics. 1980;6:226–231. [PubMed] 173. Agency for Toxic Substances and Disease Registry (ATSDR. Public Health Service. Atlanta: U.S. Department of Health and Human Services; 1999. Toxicological Profile for Lead. 174. Agency for Toxic Substances and Disease Registry (ATSDR) Case Studies in Environmental Medicine - Lead Toxicity. Atlanta: Public Health Service, U.S. Department of Health and Human Services; 1992. 175. Flora SJS, Flora GJS, Saxena G. Environmental occurrence, health effects and management of lead poisoning. In: Cascas SB, Sordo J, editors. Lead: Chemistry, Analytical Aspects, Environmental Impacts and Health Effects. Netherlands: Elsevier Publication; 2006. pp. 158–228. 176. Pirkle JL, Brady DJ, Gunter EW, Kramer RA, Paschal DC, Flegal KM, Matte TD. The decline in blood lead levels in the United States: The National Health and Nutrition Examination Surveys (NHANES) J Am Med Assoc. 1994;272:284–291. [PubMed] 177. Pirkle JL, Kaufmann RB, Brody DJ, Hickman T, Gunter EW, Paschal DC. Exposure of the U.S. population to lead: 1991–1994. Environ Health Perspect. 1998;106(11):745–750. [PMC free article] [PubMed] 178. United States Environmental Protection Agency (U.S. EPA) Lead Compounds. Technology Transfer Network- Air Toxics Website. 2002 Online at: http://www.epa.gov/cgi-bin/epaprintonly.cgi. 179. Kaul B, Sandhu RS, Depratt C, Reyes F. Follow-up screening of lead-poisoned children near an auto battery recycling plant, Haina, Dominican Republic. Environ Health Perspect. 1999;107(11):917–920. [PMC free article] [PubMed] 180. Ong CN, Phoon WO, Law HY, Tye CY, Lim HH. Concentrations of lead in maternal blood, cord blood, and breast milk. Arch Dis Child. 1985;60:756–759. [PMC free article] [PubMed] 181. Corpas I, Gaspar I, Martinez S, Codesal J, Candelas S, Antonio MT. Testicular alterations in rats due to gestational and early lactational administration of lead. Report Toxicol. 1995;9:307–313. [PubMed] 182. Andrews KW, Savitz DA, Hertz-Picciotto I. Prenatal lead exposure in relation to gestational age and birth weight: a review of epidemiologic studies. Am J Ind Med. 1994;26:13–32. [PubMed] 183. Huel G, Tubert P, Frery N, Moreau T, Dreyfus J. Joint effect of gestational age and maternal lead exposure on psychomotor development of the child at six years. Neurotoxicol. 1992;13:249–254. [PubMed] 184. Litvak P, Slavkovich V, Liu X, Popovac D, Preteni E, Capuni-Paracka S, Hadzialjevic S, Lekic V, Lolacono N, Kline J, Graziano J. Hyperproduction of erythropoietin in nonanemic lead-exposed children. Environ Health Perspect. 1998;106(6):361–364. [PMC free article] [PubMed] 185. Amodio-Cocchieri R, Arnese A, Prospero E, Roncioni A, Barulfo L, Ulluci R, Romano V. Lead in human blood form children living in Campania, Italy. J Toxicol Environ Health. 1996;47:311–320. [PubMed] 186. Hertz-Picciotto I. The evidence that lead increases the risk for spontaneous abortion. Am J Ind Med. 2000;38:300–309. [PubMed] 187. Apostoli P, Kiss P, Stefano P, Bonde JP, Vanhoorne M. Male reproduction toxicity of lead in animals and humans. Occup Environ Med. 1998;55:364–374. [PMC free article] [PubMed] 188. Flora SJS, Saxena G, Gautam P, Kaur P, Gill KD. Lead induced oxidative stress and alterations in biogenic amines in different rat brain regions and their response to combined administration of DMSA and MiADMSA. Chem Biol Interac. 2007;170:209–220. [PubMed] 189. Hermes-Lima M, Pereira B, Bechara EJ. Are free radicals involved in lead poisoning? Xenobiotica. 1991;8:1085–1090. [PubMed] 190. Jiun YS, Hsien LT. Lipid peroxidation in workers exposed to lead. Arch Environ Health. 1994;49:256–259. [PubMed] 191. Bechara EJ, Medeiros MH, Monteiro HP, Hermes-Lima M, Pereira B, Demasi M. A free radical hypothesis of lead poisoning and inborn porphyrias associated with 5-aminolevulinic acid overload. Quim Nova. 1993;16:385–392. 192. Yedjou CG, Steverson M, Paul Tchounwou PB. Lead nitrate-induced oxidative stress in human liver carcinoma (HepG2) cells. Metal Ions Biol Med. 2006;9:293–297. 193. Yedjou CG, Milner J, Howard C, Tchounwou PB. Basic apoptotic mechanisms of lead toxicity in human leukemia (HL-60) cells. Intl J Environ Res Public Health. 2010;7(5):2008–2017. [PMC free article] [PubMed] 194. Goldstein G. Evidence that lead acts as a calcium substitute in second messenger metabolism. Neurotoxicol. 1993;14:97–102. [PubMed] 195. Simons T. Lead-calcium interactions in cellular lead toxicity. Neurotoxicol. 1993;14:77–86. [PubMed] 196. Vijverberg HPM, Oortgiesen M, Leinders T, van Kleef RGDM. Metal interactions with voltage- and receptor-activated ion channels. Environ Health Perspect. 1994;102(3):153–158. [PMC free article] [PubMed] 197. Schanne FA, Long GJ, Rosen JF. Lead induced rise in intracellular free calcium is mediated through activation of protein kinase C in osteoblastic bone cells. Biochim Biophys Acta. 1997;1360(3):247–254. [PubMed] 198. Waalkes MP, Hiwan BA, Ward JM, Devor DE, Goyer RA. Renal tubular tumors and a typical hepper plasics in B6C3F, mice exposed to lead acetate during gestation and lactation occur with minimal chronic nephropathy. Cancer Res. 1995;55:5265–5271. [PubMed] 199. Goyer RA. Lead toxicity: current concerns. Environ Health Prospect. 1993;100:177–187. [PMC free article] [PubMed] 200. International Agency for Research on Cancer (IARC) In IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. Supplement 7. Volumes 1–42. Lyons, France: IARC; 1987. Overall Evaluation of Carcinogenicity: An updating of Monographs; pp. 230–232. 201. Yang JL, Wang LC, Chamg CY, Liu TY. Singlet oxygen is the major species participating in the induction of DNA strand breakage and 8-hydrocy-deoxyguanosine adduct by lead acetate. Environ Mol Mutagen. 1999;33:194–201. [PubMed] 202. Lin RH, Lee CH, Chen WK, Lin-Shiau SY. Studies on cytotoxic and genotoxic effects of cadmium nitrate and lead nitrate in Chinese hamster ovary cells. Environ Mol Mutagen. 1994;23:143–149. [PubMed] 203. Dipaolo JA, Nelson Rh, Casto BC. In-vitro neoplastic transformation of Syrian hamster cell by lead acetate and its relevance to environmental carcinogenesis.Br J Cancer. 1978;38:452–455. [PMC free article] [PubMed] 204. Hwua YS, Yang JL. Effect of 3-amonotriazole on anchorage independence and multgenicity in cadmium-treated and lead-treated diploid human fibroblasts.Carcinogenesis. 1998;19:881–888. [PubMed] 205. Roy N, Rossman T. Mutagenesis and comutagenesis by lead compounds. Mutat Res. 1992;298:97–103. [PubMed]

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