TY - JOUR AU - Sarkar, Bibudhendra AB - Abstract This paper presents an overview of the global extent of naturally occurring toxic metals in groundwater. Adverse health effects attributed to the toxic metals most commonly found in groundwater are reviewed, as well as chemical, biochemical, and physiological interactions between these metals. Synergistic and antagonistic effects that have been reported between the toxic metals found in groundwater and the dietary trace elements are highlighted, and common behavioural, cultural, and dietary practices that are likely to significantly modify health risks due to use of metal-contaminated groundwater are reviewed. Methods for analytical testing of samples containing multiple metals are discussed, with special attention to analytical interferences between metals and reagents. An overview is presented of approaches to providing safe water when groundwater contains multiple metallic toxins. Graphical Abstract Open in new tabDownload slide This review integrates recent research in hydrogeology, water testing, and metal toxicity, emphasizing interactions between toxic metals. Introduction Over the past 25 years, a health crisis of epic proportions has emerged in the Bengal Delta due to populations switching to groundwater for drinking, cooking, and irrigation rather than surface water. The switch away from using surface water for drinking and cooking was initially hailed as a tremendous boon for public health because of dramatic declines in mortality due to water-borne diseases. However, unbeknownst to the installers of the wells which made this switch possible, groundwater in the region is commonly contaminated with arsenic, manganese, uranium and other toxic metals of hydro-geological origin. In this paper, we present an overview of the global extent of naturally occurring toxic metals in groundwater, noting that multiple metal contamination of groundwater is an issue of global concern, and the risks may be further magnified by climate change. Several metals that occur as natural contaminants of groundwater are associated with severe and potentially lethal adverse health effects, including arsenic, manganese, and uranium. We review the adverse health effects attributed to the toxic metals most commonly found in groundwater, both individually and in combination with each other. We emphasize that exposure to these toxic metals most often involves exposure to a combination of toxic metals rather than to just a single metal; thus, accurate assessment of health risks due to drinking metal-contaminated groundwater must take into account potential interactions between the metals on the chemical, biochemical, and physiological levels. Health effects due to co-exposures to toxic metals are further affected by behavioural and cultural practices (e.g. smoking, sun avoidance) and dietary habits. In this paper, we highlight synergistic and antagonistic effects that have been reported between the toxic metals found in groundwater and the dietary trace elements and we also discuss behavioural, cultural, and dietary practices that are likely to significantly modify health risks due to use of metal-contaminated groundwater. We provide an overview of analytical testing for multiple metals, noting the special considerations that must be taken to avoid analytical interferences when samples contain mixtures of metals. We conclude with a brief summary of current approaches and technologies for providing safe water when groundwater contains multiple metallic toxins. Toxic metals in groundwater The discovery of toxic metals in groundwater Finding sources of pure water is an age-old problem for humans. In desert regions, people have long resorted to wells in order to access water. Folk wisdom of the desert, however, advises users to observe the behaviour of animals, and to avoid wells that animals would not drink from.1 In 1918, this folk wisdom received its first scientific confirmation that water from certain wells is contaminated and causes disease.2 Dr Abel Ayerza, a professor at the Buenos Aires Medical School, reported that a number of villagers from Cordoba had developed palmar keratosis and melanoma, and he argued that this was due to arsenic in the region's groundwater. He described a patient with weeping sores on his lower legs and discoloured toes, whose feet eventually had to be amputated, and patients with liver and heart problems or general weakness. He suggested that problems with the arterial system and the heart were due to the effects of arsenic and vanadium in combination. He noted that villagers were very much aware that some waters in the region were unhealthy despite having no bad taste or colour, and they would go to great lengths to access safe water, including harvesting rainwater from their “zinc” (galvanized) roofs or carrying water from afar. Ayerza observed that the spatial distribution of the contaminants seemed to be quite unpredictable, with some wells heavily contaminated while neighbouring wells had safe water, and he cautioned that foods in the area were also likely to contain high levels of arsenic. Subsequent research in many other parts of the globe has confirmed and replicated Ayerza's observations made almost a century ago on the serious health risks of drinking groundwater contaminated with toxic metals and the difficulty of predicting which wells may be affected. Because groundwater is generally safe, and is almost universally preferable to surface water in terms of biological contaminants, the possibility that it may contain toxic metals has not been considered until widespread health problems have arisen. Throughout the twentieth century, increasing dependence on groundwater due to migration, population pressure, or the introduction of new water technologies, has brought about epidemics of keratosis, blackfoot disease, skeletal fluorosis and other results of metal contamination due to natural sources (e.g.arsenic: Taiwan,3 Chile,4 China,5 Vietnam,6 Burkina Faso.7 In terms of numbers of people affected, arsenic contamination of groundwater in the Bengal Basin has presented the most alarming case, where 60–65 million people8 are estimated to be drinkingwater with excess levels of arsenic. Due to the extent of the contamination and the numbers of people affected, groundwater contamination has been examined more methodically and documented to a greater extent in Bangladesh than in any other country, with national surveys for arsenic in 19979 and multiple metals in 1998–1999.10 These national surveys detected high concentrations of manganese and other toxic metals besides arsenic before any resulting health effects were observed. In other regions, groundwater has typically been tested only after health has been compromised, and sampling has been regional rather than national. However, more researchers are now considering the possibility of multiple-metal contamination, and routinely screening their samples for the presence of such multiple toxins such as manganese, lead, and fluoride, rather than testing for only a single element such as arsenic. As a result, multiple metal contamination of groundwater is now being reported in many regions; see Table 1, Fig. 1. Table 1 Regions with naturally occurring multiple toxic metals in groundwater Country . Co-contaminants reported . China Arsenic, selenium11 Arsenic, manganese, uranium, iron12 Arsenic, nickel, iron13 Taiwan Arsenic, manganese, iron14 Malaysia Arsenic, manganese, uranium15 Mekong River Delta (Cambodia and Vietnam) Arsenic, manganese, cadmium, lead, nickel, selenium, barium16 Arsenic, manganese, lead, barium17 Arsenic, manganese, barium18 Arsenic, manganese, iron19 Arsenic, manganese16,20 Bangladesh Arsenic, manganese, uranium, boron21 Arsenic, manganese, nickel, chromium10b Arsenic, manganese22 India Arsenic, lead, aluminium, cadmium23 Arsenic, manganese, iron24 Arsenic, iron25 Lead, iron26 Manganese, zinc27 Iran Arsenic, cadmium, selenium28 Uganda Manganese, uranium, cadmium, lead, nickel, barium, iron29 Burkina Faso Arsenic, manganese, molybdenum7 Mali Manganese, uranium30 Ghana Arsenic, manganese, iron31 Finland Arsenic,32 uranium,33 manganese, iron34 Italy Arsenic, vanadium35 Greece Arsenic, manganese, uranium36 Arsenic, manganese, antimony37 Canada Arsenic, manganese, iron38 Arsenic, uranium39 United States Arsenic, manganese, uranium, selenium, molybdenum, boron40 Arsenic, manganese, uranium, iron41 Arsenic, manganese42 Selenium, boron43 Argentina Arsenic, manganese, uranium, vanadium, iron, strontium, boron, molybdenum44 Arsenic, uranium, vanadium, selenium45 Arsenic, lithium, cesium, boron46 Arsenic, vanadium2 Country . Co-contaminants reported . China Arsenic, selenium11 Arsenic, manganese, uranium, iron12 Arsenic, nickel, iron13 Taiwan Arsenic, manganese, iron14 Malaysia Arsenic, manganese, uranium15 Mekong River Delta (Cambodia and Vietnam) Arsenic, manganese, cadmium, lead, nickel, selenium, barium16 Arsenic, manganese, lead, barium17 Arsenic, manganese, barium18 Arsenic, manganese, iron19 Arsenic, manganese16,20 Bangladesh Arsenic, manganese, uranium, boron21 Arsenic, manganese, nickel, chromium10b Arsenic, manganese22 India Arsenic, lead, aluminium, cadmium23 Arsenic, manganese, iron24 Arsenic, iron25 Lead, iron26 Manganese, zinc27 Iran Arsenic, cadmium, selenium28 Uganda Manganese, uranium, cadmium, lead, nickel, barium, iron29 Burkina Faso Arsenic, manganese, molybdenum7 Mali Manganese, uranium30 Ghana Arsenic, manganese, iron31 Finland Arsenic,32 uranium,33 manganese, iron34 Italy Arsenic, vanadium35 Greece Arsenic, manganese, uranium36 Arsenic, manganese, antimony37 Canada Arsenic, manganese, iron38 Arsenic, uranium39 United States Arsenic, manganese, uranium, selenium, molybdenum, boron40 Arsenic, manganese, uranium, iron41 Arsenic, manganese42 Selenium, boron43 Argentina Arsenic, manganese, uranium, vanadium, iron, strontium, boron, molybdenum44 Arsenic, uranium, vanadium, selenium45 Arsenic, lithium, cesium, boron46 Arsenic, vanadium2 Open in new tab Table 1 Regions with naturally occurring multiple toxic metals in groundwater Country . Co-contaminants reported . China Arsenic, selenium11 Arsenic, manganese, uranium, iron12 Arsenic, nickel, iron13 Taiwan Arsenic, manganese, iron14 Malaysia Arsenic, manganese, uranium15 Mekong River Delta (Cambodia and Vietnam) Arsenic, manganese, cadmium, lead, nickel, selenium, barium16 Arsenic, manganese, lead, barium17 Arsenic, manganese, barium18 Arsenic, manganese, iron19 Arsenic, manganese16,20 Bangladesh Arsenic, manganese, uranium, boron21 Arsenic, manganese, nickel, chromium10b Arsenic, manganese22 India Arsenic, lead, aluminium, cadmium23 Arsenic, manganese, iron24 Arsenic, iron25 Lead, iron26 Manganese, zinc27 Iran Arsenic, cadmium, selenium28 Uganda Manganese, uranium, cadmium, lead, nickel, barium, iron29 Burkina Faso Arsenic, manganese, molybdenum7 Mali Manganese, uranium30 Ghana Arsenic, manganese, iron31 Finland Arsenic,32 uranium,33 manganese, iron34 Italy Arsenic, vanadium35 Greece Arsenic, manganese, uranium36 Arsenic, manganese, antimony37 Canada Arsenic, manganese, iron38 Arsenic, uranium39 United States Arsenic, manganese, uranium, selenium, molybdenum, boron40 Arsenic, manganese, uranium, iron41 Arsenic, manganese42 Selenium, boron43 Argentina Arsenic, manganese, uranium, vanadium, iron, strontium, boron, molybdenum44 Arsenic, uranium, vanadium, selenium45 Arsenic, lithium, cesium, boron46 Arsenic, vanadium2 Country . Co-contaminants reported . China Arsenic, selenium11 Arsenic, manganese, uranium, iron12 Arsenic, nickel, iron13 Taiwan Arsenic, manganese, iron14 Malaysia Arsenic, manganese, uranium15 Mekong River Delta (Cambodia and Vietnam) Arsenic, manganese, cadmium, lead, nickel, selenium, barium16 Arsenic, manganese, lead, barium17 Arsenic, manganese, barium18 Arsenic, manganese, iron19 Arsenic, manganese16,20 Bangladesh Arsenic, manganese, uranium, boron21 Arsenic, manganese, nickel, chromium10b Arsenic, manganese22 India Arsenic, lead, aluminium, cadmium23 Arsenic, manganese, iron24 Arsenic, iron25 Lead, iron26 Manganese, zinc27 Iran Arsenic, cadmium, selenium28 Uganda Manganese, uranium, cadmium, lead, nickel, barium, iron29 Burkina Faso Arsenic, manganese, molybdenum7 Mali Manganese, uranium30 Ghana Arsenic, manganese, iron31 Finland Arsenic,32 uranium,33 manganese, iron34 Italy Arsenic, vanadium35 Greece Arsenic, manganese, uranium36 Arsenic, manganese, antimony37 Canada Arsenic, manganese, iron38 Arsenic, uranium39 United States Arsenic, manganese, uranium, selenium, molybdenum, boron40 Arsenic, manganese, uranium, iron41 Arsenic, manganese42 Selenium, boron43 Argentina Arsenic, manganese, uranium, vanadium, iron, strontium, boron, molybdenum44 Arsenic, uranium, vanadium, selenium45 Arsenic, lithium, cesium, boron46 Arsenic, vanadium2 Open in new tab Table 2 Toxic effects of arsenic Cancers Skin cancer60 Lung cancer61 Bladder and urinary tract cancers60a,62 Digestive tract cancers60a Liver cancer63 Prostate cancer64 Breast cancer65 Skin conditions Keratosis and pigment change66 Liver disease Enlargement of the liver, cirrhosis and fatty degeneration11,66a,67 Lung disease Pulmonary obstructive and restrictive effects, chronic cough and bronchitis67,68 Changes in mouse lung cells69 and cultured human lung cells70 Heart disease Arteriosclerosis, myocardial infarction, ischemic heart disease, vascular constriction, and blackfoot disease60a,71 Hypertension68d,72 Diabetes Increased risk of diabetes72b,73 Blood disorders Anaemia or leucopoenia68c Kidney disease Renal damage74 Eye disease Pterygium75 Cataracts76 Conjunctivitis77 Immune effects Reduced immune function78 Reproductive effects Endocrine disruption79 Decreased Aberrant morphology and decreased motility of sperm in rabbits81 Neurological effects Peripheral neuropathy of both sensory and motor neurons, causing numbness, loss of reflexes, and muscle weakness2,66a,68d,82 Learning disabilities in children and reduced intellectual function83 Developmental effects Adverse pregnancy outcomes: spontaneous abortion, stillbirth, and preterm delivery,84 Increased infant mortality86 Decreased weight, height, and lung capacities of children87 Cancers Skin cancer60 Lung cancer61 Bladder and urinary tract cancers60a,62 Digestive tract cancers60a Liver cancer63 Prostate cancer64 Breast cancer65 Skin conditions Keratosis and pigment change66 Liver disease Enlargement of the liver, cirrhosis and fatty degeneration11,66a,67 Lung disease Pulmonary obstructive and restrictive effects, chronic cough and bronchitis67,68 Changes in mouse lung cells69 and cultured human lung cells70 Heart disease Arteriosclerosis, myocardial infarction, ischemic heart disease, vascular constriction, and blackfoot disease60a,71 Hypertension68d,72 Diabetes Increased risk of diabetes72b,73 Blood disorders Anaemia or leucopoenia68c Kidney disease Renal damage74 Eye disease Pterygium75 Cataracts76 Conjunctivitis77 Immune effects Reduced immune function78 Reproductive effects Endocrine disruption79 Decreased Aberrant morphology and decreased motility of sperm in rabbits81 Neurological effects Peripheral neuropathy of both sensory and motor neurons, causing numbness, loss of reflexes, and muscle weakness2,66a,68d,82 Learning disabilities in children and reduced intellectual function83 Developmental effects Adverse pregnancy outcomes: spontaneous abortion, stillbirth, and preterm delivery,84 Increased infant mortality86 Decreased weight, height, and lung capacities of children87 Open in new tab Table 2 Toxic effects of arsenic Cancers Skin cancer60 Lung cancer61 Bladder and urinary tract cancers60a,62 Digestive tract cancers60a Liver cancer63 Prostate cancer64 Breast cancer65 Skin conditions Keratosis and pigment change66 Liver disease Enlargement of the liver, cirrhosis and fatty degeneration11,66a,67 Lung disease Pulmonary obstructive and restrictive effects, chronic cough and bronchitis67,68 Changes in mouse lung cells69 and cultured human lung cells70 Heart disease Arteriosclerosis, myocardial infarction, ischemic heart disease, vascular constriction, and blackfoot disease60a,71 Hypertension68d,72 Diabetes Increased risk of diabetes72b,73 Blood disorders Anaemia or leucopoenia68c Kidney disease Renal damage74 Eye disease Pterygium75 Cataracts76 Conjunctivitis77 Immune effects Reduced immune function78 Reproductive effects Endocrine disruption79 Decreased Aberrant morphology and decreased motility of sperm in rabbits81 Neurological effects Peripheral neuropathy of both sensory and motor neurons, causing numbness, loss of reflexes, and muscle weakness2,66a,68d,82 Learning disabilities in children and reduced intellectual function83 Developmental effects Adverse pregnancy outcomes: spontaneous abortion, stillbirth, and preterm delivery,84 Increased infant mortality86 Decreased weight, height, and lung capacities of children87 Cancers Skin cancer60 Lung cancer61 Bladder and urinary tract cancers60a,62 Digestive tract cancers60a Liver cancer63 Prostate cancer64 Breast cancer65 Skin conditions Keratosis and pigment change66 Liver disease Enlargement of the liver, cirrhosis and fatty degeneration11,66a,67 Lung disease Pulmonary obstructive and restrictive effects, chronic cough and bronchitis67,68 Changes in mouse lung cells69 and cultured human lung cells70 Heart disease Arteriosclerosis, myocardial infarction, ischemic heart disease, vascular constriction, and blackfoot disease60a,71 Hypertension68d,72 Diabetes Increased risk of diabetes72b,73 Blood disorders Anaemia or leucopoenia68c Kidney disease Renal damage74 Eye disease Pterygium75 Cataracts76 Conjunctivitis77 Immune effects Reduced immune function78 Reproductive effects Endocrine disruption79 Decreased Aberrant morphology and decreased motility of sperm in rabbits81 Neurological effects Peripheral neuropathy of both sensory and motor neurons, causing numbness, loss of reflexes, and muscle weakness2,66a,68d,82 Learning disabilities in children and reduced intellectual function83 Developmental effects Adverse pregnancy outcomes: spontaneous abortion, stillbirth, and preterm delivery,84 Increased infant mortality86 Decreased weight, height, and lung capacities of children87 Open in new tab Table 3 Toxic effects of manganese Neurological effects Decreased brain function in domestic animals102 Neurological deficits in nonhuman primates103 Disruptions in dopamine, norepinephrin, and acetylcholinesterase levels103 Manganism, a condition characterized by a cock-like walk,104 Compulsive behaviours, emotional lability and hallucinations, and somatisation disorder106 Violent or criminal behaviour107 Hyperactivity in children, learning disabilities, and deficits in children’s manual dexterity and rapidity, short-term memory, and visual identification56,108 Amyotrophic lateral sclerosis102 Possible increased susceptibility to prion diseases109 Liver disease Liver damage and cirrhosis in rats104 Kidney disease Nephritis in rats104 Reproductive effects Degenerative changes in rat testes104,110 Cardiovascular effects Decreased heart muscle respiration in rats111 Ear disorders Hearing loss in mice112 Developmental effects Increased infant mortality, especially with concurrent pregnancy-induced iron deficiency anaemia113 Neurological effects Decreased brain function in domestic animals102 Neurological deficits in nonhuman primates103 Disruptions in dopamine, norepinephrin, and acetylcholinesterase levels103 Manganism, a condition characterized by a cock-like walk,104 Compulsive behaviours, emotional lability and hallucinations, and somatisation disorder106 Violent or criminal behaviour107 Hyperactivity in children, learning disabilities, and deficits in children’s manual dexterity and rapidity, short-term memory, and visual identification56,108 Amyotrophic lateral sclerosis102 Possible increased susceptibility to prion diseases109 Liver disease Liver damage and cirrhosis in rats104 Kidney disease Nephritis in rats104 Reproductive effects Degenerative changes in rat testes104,110 Cardiovascular effects Decreased heart muscle respiration in rats111 Ear disorders Hearing loss in mice112 Developmental effects Increased infant mortality, especially with concurrent pregnancy-induced iron deficiency anaemia113 Open in new tab Table 3 Toxic effects of manganese Neurological effects Decreased brain function in domestic animals102 Neurological deficits in nonhuman primates103 Disruptions in dopamine, norepinephrin, and acetylcholinesterase levels103 Manganism, a condition characterized by a cock-like walk,104 Compulsive behaviours, emotional lability and hallucinations, and somatisation disorder106 Violent or criminal behaviour107 Hyperactivity in children, learning disabilities, and deficits in children’s manual dexterity and rapidity, short-term memory, and visual identification56,108 Amyotrophic lateral sclerosis102 Possible increased susceptibility to prion diseases109 Liver disease Liver damage and cirrhosis in rats104 Kidney disease Nephritis in rats104 Reproductive effects Degenerative changes in rat testes104,110 Cardiovascular effects Decreased heart muscle respiration in rats111 Ear disorders Hearing loss in mice112 Developmental effects Increased infant mortality, especially with concurrent pregnancy-induced iron deficiency anaemia113 Neurological effects Decreased brain function in domestic animals102 Neurological deficits in nonhuman primates103 Disruptions in dopamine, norepinephrin, and acetylcholinesterase levels103 Manganism, a condition characterized by a cock-like walk,104 Compulsive behaviours, emotional lability and hallucinations, and somatisation disorder106 Violent or criminal behaviour107 Hyperactivity in children, learning disabilities, and deficits in children’s manual dexterity and rapidity, short-term memory, and visual identification56,108 Amyotrophic lateral sclerosis102 Possible increased susceptibility to prion diseases109 Liver disease Liver damage and cirrhosis in rats104 Kidney disease Nephritis in rats104 Reproductive effects Degenerative changes in rat testes104,110 Cardiovascular effects Decreased heart muscle respiration in rats111 Ear disorders Hearing loss in mice112 Developmental effects Increased infant mortality, especially with concurrent pregnancy-induced iron deficiency anaemia113 Open in new tab Table 4 Toxic effects of uranium Bone effects Decreased bone formation133 Increased bone resorption134 Increased osteocalcin levels in men, particularly with current smokers134 Kidney disease Decreased kidney function135 Cardiovascular effects Increased blood pressure136 Neurological effects Changes in the brain cholinergic system in rats137 Hormonal effects Endocrine-disruptor138 Reproductive effects Disturbed follicogenesis, oocyte meiosis and oocyte morphology in mice139 Possible fertility problems and reproductive cancers138 Bone effects Decreased bone formation133 Increased bone resorption134 Increased osteocalcin levels in men, particularly with current smokers134 Kidney disease Decreased kidney function135 Cardiovascular effects Increased blood pressure136 Neurological effects Changes in the brain cholinergic system in rats137 Hormonal effects Endocrine-disruptor138 Reproductive effects Disturbed follicogenesis, oocyte meiosis and oocyte morphology in mice139 Possible fertility problems and reproductive cancers138 Open in new tab Table 4 Toxic effects of uranium Bone effects Decreased bone formation133 Increased bone resorption134 Increased osteocalcin levels in men, particularly with current smokers134 Kidney disease Decreased kidney function135 Cardiovascular effects Increased blood pressure136 Neurological effects Changes in the brain cholinergic system in rats137 Hormonal effects Endocrine-disruptor138 Reproductive effects Disturbed follicogenesis, oocyte meiosis and oocyte morphology in mice139 Possible fertility problems and reproductive cancers138 Bone effects Decreased bone formation133 Increased bone resorption134 Increased osteocalcin levels in men, particularly with current smokers134 Kidney disease Decreased kidney function135 Cardiovascular effects Increased blood pressure136 Neurological effects Changes in the brain cholinergic system in rats137 Hormonal effects Endocrine-disruptor138 Reproductive effects Disturbed follicogenesis, oocyte meiosis and oocyte morphology in mice139 Possible fertility problems and reproductive cancers138 Open in new tab Table 5 Toxic effects of lead Neurological effects Reduced children’s capacity to learn, even at very low levels of exposure141 Reduced cognitive function in older adults142 Degenerative dementia143 Bone effects Toxic systemic effects as lead is released from bones during pregnancy or menopause144 Dental caries and tooth loss in adults145 Cardiovascular effects Hypertension146 Ischemic heart disease143 Kidney disease Kidney damage in rats and humans143,147 Liver disease Liver damage in rats147 Diabetes Increased incidence of diabetes146b Reproductive disorders Reduced fertility with paternal exposure148 Eye disorders Cataracts149 Cancer Bladder cancer150 Neurological effects Reduced children’s capacity to learn, even at very low levels of exposure141 Reduced cognitive function in older adults142 Degenerative dementia143 Bone effects Toxic systemic effects as lead is released from bones during pregnancy or menopause144 Dental caries and tooth loss in adults145 Cardiovascular effects Hypertension146 Ischemic heart disease143 Kidney disease Kidney damage in rats and humans143,147 Liver disease Liver damage in rats147 Diabetes Increased incidence of diabetes146b Reproductive disorders Reduced fertility with paternal exposure148 Eye disorders Cataracts149 Cancer Bladder cancer150 Open in new tab Table 5 Toxic effects of lead Neurological effects Reduced children’s capacity to learn, even at very low levels of exposure141 Reduced cognitive function in older adults142 Degenerative dementia143 Bone effects Toxic systemic effects as lead is released from bones during pregnancy or menopause144 Dental caries and tooth loss in adults145 Cardiovascular effects Hypertension146 Ischemic heart disease143 Kidney disease Kidney damage in rats and humans143,147 Liver disease Liver damage in rats147 Diabetes Increased incidence of diabetes146b Reproductive disorders Reduced fertility with paternal exposure148 Eye disorders Cataracts149 Cancer Bladder cancer150 Neurological effects Reduced children’s capacity to learn, even at very low levels of exposure141 Reduced cognitive function in older adults142 Degenerative dementia143 Bone effects Toxic systemic effects as lead is released from bones during pregnancy or menopause144 Dental caries and tooth loss in adults145 Cardiovascular effects Hypertension146 Ischemic heart disease143 Kidney disease Kidney damage in rats and humans143,147 Liver disease Liver damage in rats147 Diabetes Increased incidence of diabetes146b Reproductive disorders Reduced fertility with paternal exposure148 Eye disorders Cataracts149 Cancer Bladder cancer150 Open in new tab Table 6 Effects of vanadium Glucose balance and weight effects Decreased fluid intake161 Weight loss in rats162 Lowered BMI in women163 Insulin mimicker, improved glucose tolerance164 Bone effects Increased bone growth165 Inhibited cancer metastasis in bone cells166 Cardiovascular effects Decreased heart rate in animals167 Lowered or increased blood pressure in animals and humans167,168 Increased total Increased triglyceride levels in impaired glucose tolerance patients170 Reproductive effects Impaired sperm morphology and motility in rabbits81 Reduced sperm count and fertility in mice171 Neurological effects Neurotoxic effects in dopaminergic neuronal cells172 Kidney effects Kidney damage in rats162,168 Immune effects Reduced immune response in rats162 Developmental effects Adverse development in rats162 Necrotic death in neonatal cardiomyocytes in rats173 Cancer Increased chromosome mutations and DNA strand breaks in mammalian cells174 Reduced chromosome mutations in rats175 Glucose balance and weight effects Decreased fluid intake161 Weight loss in rats162 Lowered BMI in women163 Insulin mimicker, improved glucose tolerance164 Bone effects Increased bone growth165 Inhibited cancer metastasis in bone cells166 Cardiovascular effects Decreased heart rate in animals167 Lowered or increased blood pressure in animals and humans167,168 Increased total Increased triglyceride levels in impaired glucose tolerance patients170 Reproductive effects Impaired sperm morphology and motility in rabbits81 Reduced sperm count and fertility in mice171 Neurological effects Neurotoxic effects in dopaminergic neuronal cells172 Kidney effects Kidney damage in rats162,168 Immune effects Reduced immune response in rats162 Developmental effects Adverse development in rats162 Necrotic death in neonatal cardiomyocytes in rats173 Cancer Increased chromosome mutations and DNA strand breaks in mammalian cells174 Reduced chromosome mutations in rats175 Open in new tab Table 6 Effects of vanadium Glucose balance and weight effects Decreased fluid intake161 Weight loss in rats162 Lowered BMI in women163 Insulin mimicker, improved glucose tolerance164 Bone effects Increased bone growth165 Inhibited cancer metastasis in bone cells166 Cardiovascular effects Decreased heart rate in animals167 Lowered or increased blood pressure in animals and humans167,168 Increased total Increased triglyceride levels in impaired glucose tolerance patients170 Reproductive effects Impaired sperm morphology and motility in rabbits81 Reduced sperm count and fertility in mice171 Neurological effects Neurotoxic effects in dopaminergic neuronal cells172 Kidney effects Kidney damage in rats162,168 Immune effects Reduced immune response in rats162 Developmental effects Adverse development in rats162 Necrotic death in neonatal cardiomyocytes in rats173 Cancer Increased chromosome mutations and DNA strand breaks in mammalian cells174 Reduced chromosome mutations in rats175 Glucose balance and weight effects Decreased fluid intake161 Weight loss in rats162 Lowered BMI in women163 Insulin mimicker, improved glucose tolerance164 Bone effects Increased bone growth165 Inhibited cancer metastasis in bone cells166 Cardiovascular effects Decreased heart rate in animals167 Lowered or increased blood pressure in animals and humans167,168 Increased total Increased triglyceride levels in impaired glucose tolerance patients170 Reproductive effects Impaired sperm morphology and motility in rabbits81 Reduced sperm count and fertility in mice171 Neurological effects Neurotoxic effects in dopaminergic neuronal cells172 Kidney effects Kidney damage in rats162,168 Immune effects Reduced immune response in rats162 Developmental effects Adverse development in rats162 Necrotic death in neonatal cardiomyocytes in rats173 Cancer Increased chromosome mutations and DNA strand breaks in mammalian cells174 Reduced chromosome mutations in rats175 Open in new tab Fig. 1 Open in new tabDownload slide Regions with naturally occurring multiple toxic metals in groundwater. Note: Many regions have not been systematically tested for multiple toxic metals in groundwater. The distribution and geology of toxic metals in groundwater In a worldwide review of regions with arsenic in groundwater, Smedley and Kinnibergh observed that arsenic-containing reservoirs tend to be either strongly reducing aquifers derived from alluvium or loess, or inland aquifers in arid or semi-arid environments.47 Both of these types of environments tend to be in geologically young sediments, in flat low-lying areas where groundwater movement is slow, thus allowing for the accumulation rather than flushing of toxic metals released from sediments. In high pH aquifers typical of arid regions, there is desorption of arsenic and other anion-forming elements, including vanadium, fluoride, selenium and uranium. In the strongly reducing aquifers found in some deltaic regions, there is desorption of arsenic and reductive dissolution of iron and manganese oxides.47 Limited flushing is also a factor that may promote elevated concentrations of manganese, particularly where there is manganese enrichment of bedrock.48 The presence of fresh organic matter is likely to be the cause of the reducing conditions which promote the release of iron and manganese as well as arsenic.12 Iron and manganese levels may also be elevated in high pH coastal plains.14,49 Heavy use of phosphatefertilizers can increase uranium content in groundwater,50 and extensive extraction of groundwater can result in increased concentration of uranium in semi-arid areas.51 Research on groundwater has found correlations and co-occurrences between metal contaminants that generally accord with the redox condition predictions. Combinations including arsenic, fluoride and/or vanadium are frequent in arid, high pH environments (e.g., Argentina,45 Mongolia12), and combinations of arsenic, manganese, lead and/or cadmium are frequent in deltaic, low pH environments (e.g. Bangladesh,10b Cambodia52). However, some common contaminants such as manganese and uranium are found in both arid and deltaic environments, often in combination with arsenic (e.g.manganese + arsenic in Argentina,45 uranium + arsenic in Bangladesh21). One strategy that has been suggested for accessing groundwater with safe levels of arsenic in deltaic regions such as Bangladesh is to drill deeper wells. However, it must be kept in mind that arsenic is not the only potential toxic metal contaminant, and that water from deeper wells may contain other toxic metals. In one study in the Kushtia region of Bangladesh, while deeper wells tended to have less arsenic, they were found to have increased levels of uranium.21b Smedley and Kinnibergh emphasized that while arsenic regions tend to share certain geological characteristics, the specific spatial distribution of arsenic contamination is highly variable,47 necessitating the testing of individual wells in high-arsenic regions. The geology and spatial distribution of other toxic contaminants in groundwater reservoirs and wells has received much less attention, but may follow the same pattern of extreme local variability. In a case of neighbourhood uranium groundwater contamination in the United States, concentrations differed widely from one well to the next.53 Unambiguous geological indicators have not been identified for predicting the presence or concentration of one element based on the presence or concentration of another element. It is not clear whether such potential indicators even exist, although Winkel et al. argue that Holocene deltaic and organic-rich surface sediments are key indicators that arsenic contamination of the aquifer is likely.54 Slow moving groundwater with limited flushing is a major risk factor for metal contamination of groundwater, especially when the aquifer occurs in newly deposited sediments. Given the unpredictability of groundwater contamination, the prudent practice would be to screen for multiple toxic elements, including especially arsenic, manganese, lead, fluoride, and uranium, whenever new groundwaters are accessed, whether for public water supply or individual private wells.53,55 Smedley and Kinnibergh noted that arsenic and fluoride are recognized as the most dangerous natural contaminants of groundwater,47 but subsequent research has shown that manganese and uranium should also be of concern. It should be noted that even in developed countries such as the United States and Canada, which have laws governing the testing of public water supplies for toxic elements, private wells are generally unregulated and are not routinely tested for toxic metals. Furthermore, established permissible limits for manganese contamination do not take into consideration recent research demonstrating that manganese is much more toxic than previously believed, especially for children.56 In developed countries, increasing migration away from urban centres is resulting in the drilling of more private wells, and in developing countries, economic gains are permitting more people to drill private wells, increasing the risk that more people will be exposed to toxic elements in groundwater in the future. Climate change and multi-metal exposure through groundwater Global climate change may also increase the numbers of people exposed to combinations of toxic elements through groundwater. With climate change, many arid regions are expected to become more arid,57 increasing dependence on groundwater while simultaneously decreasing aquifer flushing and possibly increasing uranium concentration in groundwater.51 Rising sea levels may promote migration from coastal to arid regions, increasing populations exposed to contaminated groundwater in those regions. In coastal areas, as sea levels rise, there will likely be less flushing of aquifers, resulting in greater accumulation of arsenic, manganese and other contaminants in aquifers where conditions make these elements soluble. Seawater intrusion into aquifers may also promote the release of arsenic into groundwater.58 For example, Bangladesh is located at one of the largest river deltas in the world. The Ganges, Brahmaputra, and Meghna rivers flow south through Bangladesh to the Bay of Bengal and the Indian Ocean. Most of this country is less than 12 meters above sea level. In a normal monsoon season one-third of the cultivated land is flooded with a mixture of fresh and saltwater.59 This flooding is likely to promote the spread of arsenic and other metals in groundwater through enhancing reducing conditions in the aquifers, promoting anion exchange, and causing mixing of waters from deep and shallow aquifers. A graph of arsenic concentration versusoxidation-reduction potential is shown in Fig. 2. This graph suggests that arsenic is released from solids to Bangladesh's groundwater by reduction9 (see Fig. 3). If so, by enhancing reducing conditions, flooding also promotes the release of a wide variety of other ions, such as Fe+2 and Mn+2, into groundwater. Fig. 3 and 4 show contour maps of arsenic and chloride concentration in groundwater from shallow wells (less than 30.5 meters below ground surface). The correlation of arsenic and chloride concentrations shown in these maps suggest that arsenic may be released in the presence of chloride through anion exchange.9 Thus, saltwater intrusion from seawater flooding likely releases a wide variety of other ions, such as U+4, U+6, Mn+2, Ni+2, Cr+2, or Pb+2, into groundwater by both anion and cation exchange. Currently, Bangladesh's deep aquifer is largely free of arsenic,16a enabling the population to access safe water in many parts of the country by drilling deep wells. However, as sea levels rise, the deep aquifer may become contaminated, and deep wells may no longer provide safe water, making water treatment a necessity in large portions of the country. Thus, as global climate change takes effect, there will be an increased need for understanding metal contaminants of groundwater and their potential health effects. Fig. 2 Open in new tabDownload slide Graph of arsenic concentration (mg L−1) versusoxidation-reduction potential in water from sampled Bangladeshi wells.9a Fig. 3 Open in new tabDownload slide Map of Bangladesh showing the average arsenic concentration (mg L−1) in water from tubewells less than 30.5 meters below ground surface (● = village location; Intensity of colour indicates increasing concentration).9a Fig. 4 Open in new tabDownload slide Map of Bangladesh showing the average chloride concentration (mg L−1) in water from tubewells less than 30.5 meters below ground surface (● = village location; Intensity of colour indicates increasing concentration).9a Health effects of toxic metals from groundwater Health effects of individual toxic metals from groundwater Arsenic Arsenic causes, contributes to, or has been associated with the toxic effects listed in Table 2. Arsenic is known to cross the placenta of laboratory animals and similar arsenic concentrations have been found in cord blood and maternal blood of maternal-infant pairs exposed to arsenic in drinkingwater.11 Prenatal arsenic exposure has been associated with increased incidence of arteriosclerosis, carcinogenesis and lung cancer in mature mice88 and young adults.89 Prenatal arsenic exposure is also associated with increased frequency of acute respiratory infections in infants.78c Gender differences with arsenic toxicity are commonly reported. Male subjects tend to show arsenic lesions before women, men have a higher risk of skin cancer associated with arsenic exposure, despite similar exposure levels90 and pulmonary effects associated with arsenic exposure were found to be higher in men than women.68a In contrast, bladder cancer mortality in arsenic-exposed areas in Chile was found to be higher among women than men.91 Women of child-bearing age have been found to methylatearsenic more efficiently than men,90f,92 particularly during pregnancy.93 Arsenicmethylation efficiency in pregnant women was found to be resistant to effects of malnutrition.93 Overweight women had highly efficient arsenicmethylation compared to males of normal weight;94 high body mass index (BMI) is associated with increased oestrogen levels,95 thus, it is likely that oestrogen plays a role in the gender differences with arsenicmethylation and toxicity. Despite any potential protective benefit offered by increased oestrogen levels during pregnancy, epidemiological studies still show adverse effects of arsenic on pregnancy outcomes and infant health. In addition, gestational diabetes rates were found to increase with exposure to arsenic.73f Thus, although oestrogen may provide some protection against the toxic effects of arsenic, it does not eliminate health risks due to arsenic exposure. It is also unclear whether the mother's increased methylation of arsenic extends beneficial effects to the foetus' health. More direct research on the possible role of oestrogen providing some protection against arsenic toxicity is needed, especially research that directly compares human oestrogen levels to arsenicmethylation efficiency. Susceptibility to toxic effects from arsenic has also been shown to be affected by genetic polymorphisms.92a,96 No effective treatments for chronic arsenic poisoning have been found,68a,c,97 although early health effect of arsenic (melanosis and keratosis) can be reversed by switching to water with safe levels of arsenic.98 In Taiwan, some improvement in vascular dysfunction was found after patients switched to arsenic-free water,99 but in other cases, the adverse health effects due to exposure to arsenic persist long after exposure ceases.83c Infant mortality continued to be elevated in an arsenic-affected city in Chile for 5–8 years after exposure to arsenic ceased.86 In Argentina,100 Chile,91 China,101 and Taiwan,90a excess mortality continued to be observed in arsenic-affected cities 5–25 years after arsenic treatment systems were installed; in Taiwan increased heart disease risk in arsenic affected areas began to fall appreciably only 17–25 years after exposure ceased.71d Although some participants in a study in Bangladesh of arsenic exposure and intellectual deficits in children switched to safer wells following initial testing and their urinary arsenic levels decreased, the well-switching did not eliminate the intellectual deficits associated with the arsenic exposure from the original wells.83b Manganese Manganese causes, contributes to, or has been associated with the toxic effects listed in Table 3. Despite the fact that foetuses, infants, and children might be presumed to be highly susceptible to neurological toxins, until very recently, little research has specifically examined the possible health effects of manganese exposure for children. In rats and humans manganese absorption is higher in neonates than with adults due to the immaturity of the biliary manganeseexcretion pathways.102,114 Manganese has been found to accumulate in the brain of infants and young animals.109 Manganese effects in the brain may be particularly of concern for foetuses and infants, due to the high number of transferrin receptors elaborated by neuronal cells during development, coupled with the neural cells' putative need for transferrin for their differentiation and proliferation.102 Neonatal rats have been shown to be more likely to show symptoms of manganese neurotoxicity at the same dosing level than adults.115 Formula-fed infants had higher levels of learning disabilities than breast-fed infants; one possible explanation could be the higher manganese content in infant formulas, particularly those that are soy-based.116 Hair manganese was elevated for formula-fed but not breast-fed infants.117 In two case studies of the exposure of single families exposed to manganese through drinkingwater, in each case, the youngest family member was the first to develop clinical symptoms of manganese poisoning.108a,118 In a population-based study, 10-year-old Bangladeshi children whose drinkingwater contained high levels of manganese were found to have decreased intellectual function; this effect persisted even when co-exposure to arsenic was controlled for.56a It should be noted that this study only examined children attending school, and may have inadvertently excluded those children with intellectual or behavioural impairments severe enough to prevent them from attending school. Thus, the actual deleterious effects on behaviour and learning for the total population could potentially have been stronger than those reported in the study, which only considered the subset of the population enrolled in school. In a study involving schoolchildren in Quebec, children whose water contained high levels of manganese also had elevated levels of manganese in their hair, and a greater likelihood of having learning disabilities, problematical classroom behaviours, and hyperactivity.56b One possible mechanism for manganese increasing risk of hyperactivity may be its effects on the dopaminergic and GABAergic systems.56b,119 It should be noted that the WHO drinkingwater guidelines and US EPA RfDs for manganese are based solely on studies of adult exposures109,120—according to the WHO (World Health Organization) manganese taken by the oral route is “one of the least toxic elements”,109 but this document does take into account recent findings of neurological impairment or elevated infant mortality due to manganese exposure in children.56,113 Significantly, the cognitive deficits associated with manganese exposure in Bangladeshi children, were found with total daily intake of manganese less than 4.5 mg g−1, less than the Institute of Medicine Upper Limit (IOM UL) of 6 mg g−1 for children, which was interpolated from adult risk studies.56a Blood121 and hair56b,120b,122 manganese levels have been reported higher in girls and women, and more manganese is absorbed by women than by men given similar levels of exposures.123 One possible mechanism for manganese concentrations being higher in girls and women is that low iron stores increase manganese absorption,124 and iron deficiency is common amongst menstruating women and girls. Paradoxically, saliva manganese levels have been reported higher in boys than girls125 and symptoms of manganese toxicity were observed at a greater frequency with men than with women given similar levels of exposure.120b,126 In general, hyperactivity is found to be more common amongst boys than girls;127 however, epidemiological data have not been studied to see whether this pattern might correlate with manganese exposure and body burden. Genetic factors seem to at least partially control susceptibility to manganese toxicity. Studies of occupational and environmental exposures to manganese have suggested a genetic involvement128 and there is a great degree of inter-individual variation in manganeseretention.129 Mice with Huntington's genes were found have reduced susceptibility to manganese exposure, but enhanced susceptibility to cadmium toxicity.130 It should be noted that as with arsenic exposure, many of the neurological symptoms associated with manganese exposure persist after manganese levels return to normal,102,131 although some recovery has also been observed.132 In a case study involving learning disabilities possibly associated with manganese exposure, the learning problems persisted at least 18 months after the manganese exposure ceased.108b Chelation has not been shown to reduce symptoms of neurological toxicity.105b Uranium Uranium causes, contributes to, or has been associated with the toxic effects listed in Table 4. Children may be particularly sensitive to this toxic metal both because they consume more water per body weight than adults and because the kidneys mature postnatally.53 In a case study in which a family was exposed to high levels of uranium in their drinkingwater, it was the youngest child in the family (age 3) who first manifested symptoms of kidney damage.53 Incidence of reproductive or gonadal cancer is significantly higher for New Mexico Native American children than age-matched non-Native American children.140 It has been suggested that this may be at least partially due to elevated uranium concentrations in drinkingwater.138 Lead Lead causes, contributes to, or has been associated with the toxic effects listed in Table 5. Early in the twentieth century, the adverse effects of lead exposure on reproductive health were obvious enough for authorities to restrict women of reproductive age from working in the lead industry.151 Adverse effects of lead are often worse prenatally than postnatally.152 In utero exposure to lead is associated with increased rates of schizophrenia.153 Lead is particularly toxic for neonates because of the immaturity of the blood-brain barrier.104 Cord blood levels were found to be associated with greater neurological problems with boys than with girls.154 Boys may be more susceptible to neurotoxic effects of early lead exposure, while girls may be more susceptible to immuntoxic effects.144b Genetic polymorphisms have been reported to affect leadmetabolism;155 in particular, variants in genes associated with ironmetabolism modify leadmetabolism.156 The neurotoxicological effects of lead exposure persist after the exposure ceases.157 Evidence for renal damage can persist years after exposure to lead ceases.158 Vanadium The physiological effects and toxicity of vanadium are reviewed by Coderre and Srivastava159 and Domingo.160 Vanadium causes, contributes to, or has been associated with the effects listed in Table 6. Vanadium has been shown to promote oxidative stress in rats176 and in cell culture.172,177 Hair vanadium levels were reported higher for women than men in one study.163 Nickel Exposure to nickel can lead to lung, cardiovascular, and kidney diseases and it is a potent carcinogen known to induce cancers at any site where it is administered.178 On the cellular level, it increases oxidative products and proteins.179 Most research on the health effects of nickel has been done on industrial exposures; very little is known about the health effects of chronic exposure through drinkingwater. With industrial exposures, nickel is known to increase spontaneous abortion.180 Nickel accumulates in mouse lung and kidney tissue regardless of the route of exposure.181 Rat foetal nickel concentration was found to correspond to maternal nickel concentration.182 Men retain more nickel than women.183 Individual variation in nickel toxicity suggests there may be a genetic component to susceptibility to nickel exposure.178 Chromium Chromium III is an essential element for human nutrition184 and is the form of chromium found most commonly in drinkingwater. Chromium VI is carcinogenic but drinkingwater contamination with chromium VI is generally limited to industrial exposures.185 Chromium III is poorly absorbed from the digestive tract and it is not readily taken up by cells.186 Chromium III has been found to improve glucose intolerance and insulin resistance in mice.187 Although Chromium III is generally considered non-toxic, Chromium III picolinate and tripicolinate have been associated with DNA damage through the generation of hydroxyl radicals.188 Chromium III also inhibits DNA synthesis and the fidelity of synthesome-mediated DNA replication,189 has been found to promote oxidative stress in rats,190 and has adverse effects on human dermal fibroblasts.191 Chromium III has been found to accumulate in the liver186 and has also been found to have adverse hepatic effects in humans.192 Chronic chromium exposure reduced male fertility, implantation of foetuses, and delayed sexual maturity in mice193 and was associated with aberrant morphology and decreased motility of sperm in rabbits.81 Persons with pre-existing liver or kidney disease may be exceptionally susceptible to toxic effects from chromium and exhibit signs of chromium toxicity at concentration levels that might ordinarily be considered safe.186 Iron Iron toxicity is reviewed by Papanikalaou and Pantopoulos.194 High iron in drinkingwater has been identified as a catalyst for oxidative stress, it stimulates the growth of bacteria, and it may increase the likelihood of autoimmune diseases in genetically predisposed individuals.195 Patients with Alzheimer or Parkinson disease frequently have increased brain iron content.196 Iron may also play a role in atherosclerosis and diabetes.196,197 Iron is associated with oxidative free radicals, and thus may be a factor in aging.197a Iron overload causes changes in collagen gene expression in rats and hepatic fibrosis198 and is associated with increased risk of diabetes.199 Excess iron may also contribute to eye diseases including pterygium and macular degeneration.200 Hereditary hemochromatosis makes affected people highly susceptible to iron overload; it is found in Asian as well as European populations and may be overlooked due to iron deficiency or thalassemia.201 Barium Health effects of barium in drinkingwater are reviewed by Kojola et al.202 Barium affects blood pressure in rats and may increase risk of hypertension;203 however, other studies were not able to confirm this effect.204 It may induce cardiac arrhythmias in people over age 60.202 Barium in drinkingwater may reduce incidence of dental caries.205 Combinations of toxic metals Environmental exposure to metals almost always involves simultaneous exposure to a combination of metals as well as other environmental factors.206 When water from high arsenic areas is screened for other metals, it is quite often found to have multiple elements exceeding drinkingwater guidelines (e.g.arsenic + manganese, uranium, lead, nickel, chromium, barium, and/or cadmium in South and Southeast Asia,10b,16,21,56a,207 arsenic + uranium, and/or vanadium in Argentina,2,45,100 arsenic + manganese in China:68c Studies of metal exposure frequently note evidence of co-exposure by other metals.53,56a,83a,83c,113,120a,208 In addition to exposure through drinkingwater, populations are also commonly exposed to various toxic metal through diet, smoking, drug-therapies, and alcohol intake. Smoking and use of tobacco products, including exposure to second-hand smoke, implies significant exposure to cadmium,209 and may also involve lead,145,209 vanadium,171 arsenic,209e uranium,210 antimony,209g or barium.209g For these reasons, heavy metal interactions with drinkingwater contaminants including cadmium and other metals must be considered when populations exposed to metals through drinkingwater include smokers. Environmental lead exposure is also common in countries with metal-contaminated drinkingwater, such as Bangladesh, where many children have blood lead levels above 10 μg/dl WHO guideline.211 When subjects are exposed to metals in combination, the metals may each have their own typical health effects; they may also have synergistic or antagonistic effects on each other. In calculating cancer risks due to drinkingwater contaminants, it is vital to consider not only the health risks due to individual contaminants, but also those risks due to combinations of contaminants. Effects on absorption and excretion Ingestion of metals in combination may increase or decrease the absorption of the individual metals in the digestive tract. Some metals promote the excretion of other metals. The absorption and excretion effects of metals are summarized in Table 7. Table 7 Interaction effects on absorption and excretion of metals Element . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Zinc ↓Arsenic212 ↓Lead157,213 ↓Manganese214 ↓chromium215 ↓Iron216 and haemoglobin217 Selenium ↓Arsenic218 ↓Lead157 Calcium ↓Manganese219 ↓Lead220 ↓Chromium221 ↓Iron222 ↓Zinc223 Iron ↓Arsenic69,195,224 ↓Manganese214 ↓Lead225 ↓Cadmium226 ↓Chromium215 ↓Calcium222 Chromium ↓ Lead157 Vanadium ↓ Chromium227 Barium ↑ Calcium204b Aluminium ↓ Fluoride228 Arsenic ↓ Selenium218a,c Uranium ↓ Calcium134 Nickel ↓Manganese, zinc and magnesium229 șIron230 ↓Calcium231 ↓Ascorbic acid232 Manganese ↑Cadmium157 ↓Iron104,233 ↓Zinc214 ↓Calcium231 Lead ↓Arsenic from bones234 ↓Zinc, iron and manganese from the brain235 ↓Zinc213a ↓Selenium157 Cadmium ↑Nickel236 ↓Selenium237 ↓Iron237,238 ↓Zinc214,239 ↓Calcium231,238,240 Element . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Zinc ↓Arsenic212 ↓Lead157,213 ↓Manganese214 ↓chromium215 ↓Iron216 and haemoglobin217 Selenium ↓Arsenic218 ↓Lead157 Calcium ↓Manganese219 ↓Lead220 ↓Chromium221 ↓Iron222 ↓Zinc223 Iron ↓Arsenic69,195,224 ↓Manganese214 ↓Lead225 ↓Cadmium226 ↓Chromium215 ↓Calcium222 Chromium ↓ Lead157 Vanadium ↓ Chromium227 Barium ↑ Calcium204b Aluminium ↓ Fluoride228 Arsenic ↓ Selenium218a,c Uranium ↓ Calcium134 Nickel ↓Manganese, zinc and magnesium229 șIron230 ↓Calcium231 ↓Ascorbic acid232 Manganese ↑Cadmium157 ↓Iron104,233 ↓Zinc214 ↓Calcium231 Lead ↓Arsenic from bones234 ↓Zinc, iron and manganese from the brain235 ↓Zinc213a ↓Selenium157 Cadmium ↑Nickel236 ↓Selenium237 ↓Iron237,238 ↓Zinc214,239 ↓Calcium231,238,240 Open in new tab Table 7 Interaction effects on absorption and excretion of metals Element . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Zinc ↓Arsenic212 ↓Lead157,213 ↓Manganese214 ↓chromium215 ↓Iron216 and haemoglobin217 Selenium ↓Arsenic218 ↓Lead157 Calcium ↓Manganese219 ↓Lead220 ↓Chromium221 ↓Iron222 ↓Zinc223 Iron ↓Arsenic69,195,224 ↓Manganese214 ↓Lead225 ↓Cadmium226 ↓Chromium215 ↓Calcium222 Chromium ↓ Lead157 Vanadium ↓ Chromium227 Barium ↑ Calcium204b Aluminium ↓ Fluoride228 Arsenic ↓ Selenium218a,c Uranium ↓ Calcium134 Nickel ↓Manganese, zinc and magnesium229 șIron230 ↓Calcium231 ↓Ascorbic acid232 Manganese ↑Cadmium157 ↓Iron104,233 ↓Zinc214 ↓Calcium231 Lead ↓Arsenic from bones234 ↓Zinc, iron and manganese from the brain235 ↓Zinc213a ↓Selenium157 Cadmium ↑Nickel236 ↓Selenium237 ↓Iron237,238 ↓Zinc214,239 ↓Calcium231,238,240 Element . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Zinc ↓Arsenic212 ↓Lead157,213 ↓Manganese214 ↓chromium215 ↓Iron216 and haemoglobin217 Selenium ↓Arsenic218 ↓Lead157 Calcium ↓Manganese219 ↓Lead220 ↓Chromium221 ↓Iron222 ↓Zinc223 Iron ↓Arsenic69,195,224 ↓Manganese214 ↓Lead225 ↓Cadmium226 ↓Chromium215 ↓Calcium222 Chromium ↓ Lead157 Vanadium ↓ Chromium227 Barium ↑ Calcium204b Aluminium ↓ Fluoride228 Arsenic ↓ Selenium218a,c Uranium ↓ Calcium134 Nickel ↓Manganese, zinc and magnesium229 șIron230 ↓Calcium231 ↓Ascorbic acid232 Manganese ↑Cadmium157 ↓Iron104,233 ↓Zinc214 ↓Calcium231 Lead ↓Arsenic from bones234 ↓Zinc, iron and manganese from the brain235 ↓Zinc213a ↓Selenium157 Cadmium ↑Nickel236 ↓Selenium237 ↓Iron237,238 ↓Zinc214,239 ↓Calcium231,238,240 Open in new tab Zinc absorption is also increased by concurrent protein consumption,223 but reduced by concurrent casein consumption,239 phytates, or dietary fibre.238,239 Zinc promotes absorption of vitamin A.241 During pregnancy, zinc and cadmium absorption from oral routes are increased in rats and humans.242 Iron absorption is increased by concurrent consumption of ascorbic acid243 or vitamin A,244 but decreased by concurrent consumption of chilli245 or tea.246 Chromium absorption is reduced by concurrent phytate consumption but increased by concurrent oxalate consumption.247 Manganese absorption is reduced by concurrent consumption of dietary fibre, phytates, phosphorus, oxalic acid or tannic acid.248 Since lead is associated with reduced levels of brain manganese, co-exposure to lead might reduce the neurotoxic effects of manganese. However, it is not clearly whether any potential benefits due to such exposure would outweigh the neurotoxic effects of the lead exposure itself. If nickel also reduces tissue concentrations of manganese in humans as with animals, concurrent exposure to nickel may provide some protection against exposure to manganese; however, it is also possible that ingestion of nickel could increase manganese absorption by reducing calcium stores, since concurrent calcium consumption reduces manganese absorption. It is also possible that ingestion of uranium or cadmium may increase manganese absorption by reducing calcium stores. Deficiencies of essential trace metal elements may also affect absorption of toxic metals, as summarized in Table 8. Table 8 Interaction effects of trace metal deficiencies on absorption and excretion of metals Deficiency . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Iron ↑Manganese absorption214,249 ↑Arsenic in liver250 ↑Lead absorption104,157,214,237,251 ↑Cadmium104,214,237,252 ↑Zinc214 Zinc ↑Lead213a ↑Cadmium237 Calcium ↑ Lead157,253 Deficiency . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Iron ↑Manganese absorption214,249 ↑Arsenic in liver250 ↑Lead absorption104,157,214,237,251 ↑Cadmium104,214,237,252 ↑Zinc214 Zinc ↑Lead213a ↑Cadmium237 Calcium ↑ Lead157,253 Open in new tab Table 8 Interaction effects of trace metal deficiencies on absorption and excretion of metals Deficiency . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Iron ↑Manganese absorption214,249 ↑Arsenic in liver250 ↑Lead absorption104,157,214,237,251 ↑Cadmium104,214,237,252 ↑Zinc214 Zinc ↑Lead213a ↑Cadmium237 Calcium ↑ Lead157,253 Deficiency . Interaction effects on absorption and excretion of metals (arrow shows likely direction of net interaction effect on body burden) . Iron ↑Manganese absorption214,249 ↑Arsenic in liver250 ↑Lead absorption104,157,214,237,251 ↑Cadmium104,214,237,252 ↑Zinc214 Zinc ↑Lead213a ↑Cadmium237 Calcium ↑ Lead157,253 Open in new tab Women with similar exposure histories tend to have higher levels of blood cadmium levels than men, possibly because of lower iron stores.254 Chemical interactions Elements with similar physical and chemical properties may act antagonistically by competing for transport and storage sites and displacing each other from enzymatic and receptor proteins.157,255 Conversely, they may act synergistically by promoting oxidative and other cellular damage. While additivity is generally assumed for low level co-exposures,256 synergistic cytotoxicity effects have been reported with human keratinocyte cells with chemical mixtures including arsenic, cadmium, chromium, and lead at low doses.257 Cadmium, chromium, nickel and lead may interfere with DNA repair, leading to damage not directly attributable to the heavy metals.258 Competition and antagonistic reactions Zinc, selenium, and calcium appear to provide some protection against heavy metal toxicity157,213b,259 and exposure to heavy metals can reduce the anti-oxidative functions of these essential trace elements. Interactions between metals involving oxidative stress are reviewed by Valko.260 Zinc is necessary for DNA repair, and zinc deficiency results in impaired synthesis of DNA.261 Zinc can be replaced as an enzymatic co-factor by mercury, cadmium, or lead with adverse consequences.174,262 Zinc is also important for production of metallothionein, an intracellular metal-binding protein that sequesters heavy metals.104,263 Arsenic is known to promote oxidative stress.264 Arsenic competes with zinc in metal-binding proteins involved in DNA repair265 and exposure to arsenic reduces DNA repair capability in cell culture.266 Co-administration of zinc and arsenic results in a reduction of arsenic-related liver damage in rats;224 similarly, co-administration of zinc with nickel results in a reduction of nickel-related damage.267 Selenium protects against oxidative stress through glutathione peroxidase and other antioxidant activity.218a Selenium and arsenic are chemically similar; thus, they act antagonistically in certain reactions.268 Arsenic inhibits the action of selenium, causing an apparent deficiency in the glutathione peroxidase system.11 Selenium has been found to reduce the toxicity of arsenic,259a,269 selenium deficiencies have been linked to arsenic-induced skin cancers,270 and dietary supplements with selenium may counter some degree of arsenic toxicity.271 Selenium has also been shown to have antagonistic effects on cadmium, lead and nickel,157,263,272 although in order for selenium to have significant protective effects against lead, selenium must be given at levels high enough to have its own toxic effects235 and high doses of selenium appear to exaggerate lead toxicity in rats.273 Smokers are reported to have lower serum selenium levels, and heavy smokers also have depressed serum zinc levels.274 Arsenic is methylated in the liver with an enzymatic reaction that requires glutathione and S-adenosylmethionine.275 Thus, metals that interfere with the required methylation reactions reduce the elimination of arsenic and prolong exposure, potentially increasing the toxic effects. In particular, selenium and zinc may be required for methylation reactions,276 and selenium may increase arsenicmethylation capacity,94 so exposure to arsenic may increase requirements for selenium and zinc; selenium and zinc deficiencies may increase arsenic toxicity. Oestrogen increases choline synthesis,277 which enables the formation of methionine, a necessary amino acid for arsenicmethylation. Smokers and chewers of betel quid were found to have reduced arsenicmethylation efficiency;92b smokers of bidis, hand-rolled cigarettes popular in South Asia, were found to methylatearsenic less efficiently than smokers of mass produced cigarettes.90f Chisholm suggested that heavy metals are likely to interact with immune proteins, particularly those containing sulphur.262 The toxic effects of concurrent exposure to arsenic and antimony may be sub-additive because of competition for sulfhydryl groups.278 Arsenic inhibits the increase in serum creatinine associated with cadmium,279 and lead tends to antagonize the cadmium-induced rise in N-acetyl-β-d-glucosaminidase,279 suggesting that co-exposure to arsenic and/or lead might provide some degree of protection against the renal damage due to cadmium exposure. However, synergistic effects between arsenic and cadmium on nephrotoxicity in a human population co-exposed to both metals have been reported.280 The trivalent arsenical phenylarsine oxide forms thioarsenite complexes with vicinal or paired thio groups of cellular proteins, and this has been shown to inhibit glucose transport in adipocytes.281 Zinc and selenium have been found to protect against cadmium-induced alterations in glucose tolerance282 in rats, but it is not known whether zinc and selenium can protect against arsenic-induced diabetes. Nickel antagonizes manganese-induced neurotoxicity in rats283 and depletes intracellular ascorbate.232 Mimicry is one type of competitive mechanism through which toxic metals may gain access to cells.255 Selenium may be a functional mimicker of oestrogen.255 Oestrogen has been found to provide some protection against oxidative stress mechanisms in mice.284 Other metallomimics of oestrogen include cadmium,285 antimony, arsenic, barium, chromium, lead, nickel, uranium, and vanadium.286 Carcinogenesis and synergistic effects Some metals considered carcinogenic may require co-exposure to other metals or toxins in order for carcinogenesis to occur. Alternatively, the carcinogenicity of some metals may be increased by other oxidative stressors.174 There are some indications that carcinogenesis associated with arsenic may be due to co-exposure to other carcinogens.287 Smoking involves significant exposure to cadmium, and arsenic was found to potentiate the effects of cadmium when co-ingested.288 Smoking has been associated with increased arsenic toxicity90c,d,289 and risk of skin lesions61b,90c,d,290 and lung, bladder and skin cancer is higher in smokers exposed to arsenic through drinkingwater than non-smokers or smokers who are not exposed to arsenic through drinkingwater.289a,290,291,94 Betel nut users were also found to have increased risk of developing arsenic-induced skin lesions;289b the effect of damage observed with oral mucosal cells appeared to show evidence for a synergistic rather than additive effect between betel quid use and arsenic.292 Arsenic may also act as a co-genotoxin for methyl methanesulfonate and UV-induced pyrimidine dimers.293 Mice exposed to arsenic in addition to UV-light showed greater incidence of skin cancers than mice exposed to UV-light alone287f,h,294 and human keratinocytes showed synergistic effects when exposed to UV-light in the presence of arsenic.266,295 A dose-response effect with UV and arsenic exposure was noted in humans,90e while selenium was found to block the cancer enhancement effect of arsenic but not of UVR in mice.296 Exposure to sunlight was also found to predict arsenic lesions in a Bangladeshi population.90d,297 Chen et al. also reported a possible relationship between arsenic toxicity and exposure to fertilizers, but it was not noted in that study whether socio-economic status (SES) had been taken into consideration as a potential confounding factor.90d Ingestion of arsenic has been found to increase the incidence of spontaneous viral cancers.218a Pretreatment with arsenic at low levels has been found to dramatically increase liver damage in mice exposed to lipopolysaccharide.298 Nickel may also require exposure to another toxin to potentiate its mutagenic effects;178 arsenic and nickel may act synergistically in the lungs to produce lung cancer. Nickel has been found to increase skin cancer risk with mice exposed to UVR.299 On its own, chromium III is not known to have carcinogenic effects;300 however, it could potentiate mutagenic effects of other metals by causing DNA damage.188a,301 A synergistic effect on the teratogenecity of lead and cadmium has been reported;302 lead and cadmium are also reported to interact synergistically with testicular effects,303 but co-exposure to zinc may decrease the testicular effects.304 An interaction effect on children's IQ has been reported for lead and manganese.305 A risk assessment study of metal mixtures predicted that lead may have a greater than additive effect when combined with arsenic or cadmium for neurological problems.303 It has been suggested that there could be possible synergistic effects between arsenic and antimony, due to similarities between these metals.306 Exacerbation of health effects The effective toxicity of metals may be increased when multiple metals have adverse effects on the same organs or physiological systems. Effects that might ordinarily be minor may result in critical damage when multi-metal exposure occurs. Conversely, in some instances, multi-metal exposure may provide some degree of protection against adverse effects of some metals. Brain and central nervous system Heavy metal exposure has been found to be above average in violent or aggressive persons.107b,307 Peripheral neuropathy due to arsenic68c may be particularly debilitating if there is co-exposure to manganese, which causes tremors and loss of balance105a and is associated with somatisation disorder.106 Iron deficiency anaemia increases manganese concentrations in the brain,308 and manganese exposure with concurrent iron deficiency magnified deleterious manganese effects in the rat brain,309 making manganese exposure particularly problematic for those with iron deficiency anaemia or low iron intake, especially since iron deficiency anaemia is also linked to increased absorption of lead and cadmium, which each have their own toxic neurological effects. This is of special concern in South Asia where iron deficiency anaemia is endemic310 and manganese concentrations in the drinkingwater are frequently high, and concurrent exposures to lead or cadmium are common. In addition, iron deficiency anaemia is independently associated with problems of neurological development and lower mental and motor test scores311 and increased levels of neuropsychiatric symptoms106 and iron stores, like manganese, affect the dopaminergic system.106 Zinc is essential for the development and function of the nervous system.261 Zinc deficiency impairs brain function216,261,312 and is associated with increased levels of depression;313 since nickel, lead, and cadmium exposure reduce zinc absorption and increase zincexcretion, they may indirectly affect brain function by reducing essential zinc stores. Neurobehavioral effects and learning disabilities associated with childhood exposure to one toxic metal may be increased synergistically when exposure is to multiple metals. The blood-brain barrier develops only during the first year of life, increasing risks associated with toxic metal exposures to foetus and neonates. Visual-motor performance deficits were reported in children exposed to arsenic and lead in combination, as well as possible problems with attention deficit and distractibility.83a,208a,314 Mentally retarded and learning disabled children show higher than average levels of toxic metals, particularly cadmium and lead.314a,315 Arsenic, and manganese have been independently linked to intelligence deficits and learning disabilities in children; in the absence of evidence for antagonistic effects between these two metals, it is likely that adverse effects due to co-exposure to these metals is at least additive, and further exacerbated by co-exposure to lead. Kidneys, bones, and hypertension The kidneys reabsorb and accumulate bivalent metals, and they are the main route of excretion for heavy metals, making them particularly susceptible to toxicity from heavy metals.316 It has been suggested that if body stores of selenium are low, arsenic will be excreted through the kidneys, increasing risk of kidney and bladder cancer.218a Metallothionein may be responsible for selective accumulation of cadmium in the kidneys, potentiating the nephrotoxic effects of this metal.157,253 It is possible that kidney damage associated with other toxic metals may be due to a similar mechanism. Kidney damage has been observed in children with low level exposures to mixtures of cadmium, mercury, lead, and arsenic.279 A risk assessment study of mixtures of metals predicted that cadmium, arsenic, lead and chromium(vi) will have a less than additive risk for renal effects;303 concurrent exposure to lead and cadmium resulted in lower than expected renal effects in rats.288 In contrast, mice who consumed both arsenic and cadmium showed greater renal effects than when fed either arsenic or cadmium alone.317 Persons with renal insufficiency show increased levels of blood vanadate with vanadium exposure,318 thus co-exposure to metals associated with kidney damage is of special concern when there is exposure to vanadium. Exposure to uranium through drinkingwater has been associated with disturbances of iron homeostasis in the kidney in rats319 and causes kidney damage.135a,320 Nickel, lead, chromium and vanadium exposure are also associated with kidney damage.162,178,321 Patients with kidney disease are advised to restrict intake of chromium because of increased susceptibility to its toxic effects,322 thus exposure to chromium at levels that might ordinarily be considered safe may have increased adverse effects for persons with concurrent exposure to arsenic, uranium, nickel, or lead exposure. Renal disease is also associated with zinc deficiency,323 which is promoted by ingestion of lead, nickel, or cadmium. Chronic renal insufficiency is associated with changes in bone metabolism.324 Kidney damage due to cadmium exposure increases levels of bone resorption markers and may induce osteoporosis through increasing excretion of calcium.240a,325 Cadmium exposure concurrent with low calcium intake may result in Itai-Itai disease.326 Exposure to uranium likewise increases bone resorption markers;134 this is of particular concern for smokers drinkinguranium-enriched water due to their concurrent exposure to cadmium through smoking. Iron deficiency has been shown to decrease bone density in rats.327 Through causing renal insufficiency, metals associated with kidney damage, including uranium, nickel, lead, and chromium may increase risk of osteoporosis, particularly with smokers, who have additional exposure to cadmium, and exposure to uranium, nickel, lead, or chromium may be of added concern for populations with high rates of iron deficiency. Arsenic,72a,328 uranium136 and lead146b exposure have been independently shown to be associated with hypertension. Hypertension is known to be a risk factor for kidney disease and kidney disease itself is also associated with increased levels of hypertension.329 Thus, concurrent exposure to a combination of metals including arsenic, uranium, manganese, nickel, lead, or chromium may synergistically bring about both hypertension and kidney disease; these effects may be further exacerbated by smoking, which is also independently associated with increased hypertension and additional exposure to cadmium, which is itself associated with renal damage.330 Hormones, reproductive system, and fertility Gender differences in arsenic symptoms suggest that oestrogen may provide some protection against arsenic toxicity. Oestrogen may also protect against bone resorption due to uranium exposure.134 Uranium seems to have estrogenic activity.138 It is an open question whether exposure to uranium might mitigate some amount of arsenic toxicity through these estrogenic effects. Arsenic exposure in utero has been found to affect genes encoding oestrogensignalling in mice.331 Zinc supplementation can reduce manganese-induced testicular damage and neurotoxicity.283,332 Cadmium and arsenic are likely endocrine disruptors,333 which may be linked to increased prostate cancer risk associated with exposure to these toxins;334 as an oestrogen mimicker, cadmium may have adverse effects for female offspring.144b Population fertility rates are likely to be affected through exposures to combinations of metals. Population fertility is likely to be lowered because of reduced testosterone levels and erectile dysfunction due to arsenic exposure,80 testes damage due to manganese exposure,110 reduced male fertility due to lead,148 chromium,322 vanadium171 or molybdenum335 exposure, reduced sperm motility due to arsenic, chromium, or vanadium exposure,81 oocyte or follicular changes due to uranium exposure,138,139 reduced implantation due to chromium exposure,193 delayed sexual maturity due to chromium exposure,193 and increased chance of spontaneous abortion and infant mortality due to arsenic, manganese or nickel exposure, acting alone or in combination.84a,b,84d,86,180,336 However, in one study in Bangladesh, excess infant mortality due to manganese exposure may have been reduced in areas with co-exposure to arsenic,113 although SES may have been a potential confounding factor in that study. Pancreas and glucose balance Chromium III and vanadium can reduce blood glucose levels or improve glucose tolerance.164c,227,337 Thus, it is conceivable that consuming water with high levels of chromium or vanadium could provide some protection against adverse effects of arsenic or lead on promoting diabetes. Zinc and selenium may also potentially improve glucose tolerance under conditions of toxic metal exposure.255,282 Zinc is required for the normal function of the pancreas216 and zinc deficiency may promote the development of diabetes;338 thus, exposure to metals which reduce zinc absorption or increase zincexcretion such as lead, cadmium, and nickel, may increase risk of glucose imbalance. Cadmium can also promote hyperglycaemia,339 which may further increase risk of diabetes for smokers in populations exposed to arsenic, lead, and/or nickel through drinkingwater. Liver Concurrent liver disease predisposes patients to symptoms of manganese toxicity under conditions of manganese exposure.128 If liver function is compromised, manganese is not excreted normally, and may result in increased accumulation in the brain,340 where it may cause neurological problems. Arsenic causes liver damage68c,341 and exposure to arsenic increased liver iron concentration in rats.288 Patients with liver disease are advised to limit intake of chromium because of risk of further liver damage.186 Thus, arsenic and chromium exposure are of particular concern if there is concurrent manganese exposure since they may worsen hepatic problems due to the multi-metal exposure and exacerbate neurological problems due to the manganese exposure. Iron-deficiency anaemia has been found to exaggerate hepatic effects of manganese exposure.249b Zinc deficiency is common in patients with cirrhosis,216 thus arsenic-induced liver damage may reduce zinc stores, resulting in adverse systemic effects from reductions in this essential anti-oxidant. Pulmonary system Arsenic exposure may be particularly dangerous for smokers because of the synergistic effects of co-carcinogens such as cadmium and other heavy metals contained in cigarette smoke.209a Also, the increased levels of pulmonary disease found with smokers may be exacerbated by exposure to arsenic since arsenic in the absence of smoking has been found to increase levels of chronic cough and chronic bronchitis.68c Low levels of antioxidants in the lungs may potentiate the adverse effects of arsenic in the pulmonary system.218a Concurrent exposure to arsenic and nickel is of particular concern because both metals are associated with lung diseases. Cardiovascular system Insufficient dietary chromium is associated with increased cardiovascular problems,227 thus concurrent chromium exposure may provide some protection against cardiovascular effects of other metals. Vanadium has been shown to provide some protection against hypertension and vascular diseases,342 so co-exposure to vanadium may decrease cardiac effects of other metals. Both arsenic exposure and nickel exposure have been shown independently to be associated with increased risk of myocardial infarction.68c,178 Thus, concurrent exposure to both arsenic and nickel could potentially further increase this risk. Possible synergistic effects between arsenic and cadmium have been reported for rat heart tissue.343 Dietary interactions with groundwater toxic metals Additional exposure to metals through food For many metals, exposure through drinkingwater is supplemented by exposure through food. Dietary exposure to manganese123 and vanadium171 generally exceeds exposure through drinkingwater. This must be considered when calculating drinkingwater guidelines, since drinkingwater is responsible for supplemental, not sole exposure to metals. Rice, in particular, concentrates arsenic, and contains as much as 10 times the arsenic content as other foods;344 rice is the predominant dietary contributor of inorganic arsenic.11,345 In South Asian regions where groundwater is contaminated by arsenic and rice consumption is high, rice contributes approximately half of daily exposure to arsenic.344–346 Arsenic also accumulates in the skins of root vegetables;346j however, in Bangladesh, rice contributes a substantially higher proportion of arsenic to the diet than other vegetables or legumes.345 Dietary supplementation of arsenic is a more significant factor for those whose drinkingwater contains lower levels of toxic metals.346g,h,347 It has been noted that laboratory studies with animals involving low-dose exposure to arsenic in drinkingwater can be confounded by arsenic that is incidentally supplied in standard laboratory feed.348 While total dietary exposure to manganese is generally highest from food sources,349 manganese has greatest bioavailability in water.350 In foods, manganese levels tend to be relatively low in meats and poultry and higher in nuts, cereals, legumes, and leafy greens;248 blood manganese concentration has been found to be related to frequency of consumption of grains and leafy greens.121 Vegetarian diets may be higher in manganese than non-vegetarian diets.351 Tea is particularly high in manganese, but tannins greatly reduce its bioavailability from this source.248,352 Cadmium levels in food, while generally low, are highest in grains, leafy vegetables, root vegetables, organ meats, and shellfish,353 and rice grown in cadmium-contaminated soils.354 Uranium levels tend to be higher in root vegetables than other foods.50 Certain meat products in Pakistan and India have been found to contain unacceptably high levels of arsenic, cadmium, and lead; the Pakistani products also contain relatively low levels of zinc.355 Drinking water provides only a minor component of overall intake of zinc.216 Zinc is most commonly obtained from and most absorbable from animal products261,356 and a high-protein diet is probably necessary in order to obtain recommended daily allowances of zinc from food.357 Vegetarian diets tend to result in less zinc absorbance than diets that include meat.358 The only significant dietary source of selenium is animal protein, and the levels of selenium in animal protein are dependent on the selenium levels of the plants consumed by the animals, which are in turn, dependent on the selenium content of the soils and irrigation water.218a Elevated levels of arsenic, iron, and manganese were found in soils that received irrigation from groundwater with high concentrations of these contaminants, which could lead to elevated levels of these contaminants in crops.359 Vegetables irrigated with arsenic-rich water have elevated levels of arsenic,346d,k,360 as does tobacco.361 Rice straw is used as animal feed in Bangladesh, and may contribute to arsenic levels in beef.360a Foods grown in Bangladesh and imported to the UK contained 2 to 100 times as much arsenic as similar foods grown in the UK.346c Arsenic content of food was also found to be high in a region of Thailand.362 It has also been suggested that fertilizer and pesticide use may contribute to heavy metal contamination of soils.363 Both soy and rice are known to accumulate manganese.114 Grains and rice may accumulate cadmium if grown in polluted soil or irrigated with contaminated water157,364 and tobacco naturally accumulates cadmium.365 Cadmium levels in Bangladeshi vegetables were lower than those reported in the developed world, but lead levels were higher; zinc levels were also lower.360b In a market basket survey in Bangladesh, dietary intake of manganese and nickel was high, while zinc intake was low;346a however, zinc content of vegetables grown in one region of Bangladesh was high.363 Lead content in chicken eggs has been found to correlate with lead concentrations in soil.366 Preparation and cooking methods can alter the arsenic content and arsenic species found in food.367 Rice cooked in high-arsenic water contained twice as much arsenic as raw rice;347a,368 milling rice or parboiling in arsenic-free water can reduce the arsenic content of cooked rice.360c Even when safe drinkingwater is provided, arsenic levels in hair may still be elevated due to continuing to cook food in arsenic-contaminated water.369 Arsenic levels in cooked food in Bangladesh correlated with arsenic levels in household drinkingwater.346h Beans and legumes absorb arsenic when cooked in water containing arsenic.370 This is of particular concern for vegetarians and people of lower SES in South Asia who often eat legumes in place of meat. Some studies have found reduced arsenic symptoms amongst people who eat animal protein, but one explanation for this finding could be that people who consume little animal protein also consume relatively large amounts of beans and legumes, which when cooked in arsenic-contaminated water, may increase their arsenic exposure. The concentrations of other metals in cooked foods and possible effects of cooking methods have not been studied; for instance, it is not known how total manganese content and bioavailability in tea may be affected by the manganese concentration of the water with which the tea is made. The metallic composition of cooking and serving dishes and potential for leaching metals also needs to be considered when calculating total metal exposure. Leaching from kitchen utensils and water pipes can add significantly to daily intake of nickel, chromium, and lead.227,371 Chromium exposure may be increased when acidic food is prepared or served in stainless steel utensils;186 such utensils are commonly used as serving dishes throughout South Asia. Glass dinnerware, glazed ceramic tea mugs, and pressure cookers produced in India were found to leach lead, cadmium, manganese, nickel, chromium, iron, and/or zinc.372 Interactions with dietary components and deficiencies Certain dietary constituents affect absorption of metals. Nutritional deficiencies and general nutritional levels also affect the outcomes of exposures to toxic metals. Protein S-adenosylmethionine levels in rats are dependent on dietary consumption of methionine and choline;373 adequate protein intake has been identified as the most important dietary factor affecting arsenic toxicity.263 Low protein diets have also been found to be associated with reduced arsenicmethylation efficiency and greater arsenic toxicity71a,289b,374 and subjects who consumed higher levels of animal protein seemed to have decreased adverse health effects due to arsenic exposure.346h Protein intake also affects lead toxicity375 and low protein diets increase absorption of cadmium in animals.263 It should be noted that studies comparing arsenic toxicity to animal protein intake may have zinc and/or selenium intake as a confounding factor, since intake of zinc and selenium are strongly correlated with animal protein intake, and zinc and selenium likely reduce arsenic toxicity. Thus, further study is needed to differentiate the effects that zinc, selenium, protein, and animal protein have on arsenic and other metal toxicity. Vitamins B vitamins have been identified as essential for arsenicmethylation reactions.297,346h,376 Increased intake of B vitamins reduces arsenic toxicity297,346 and people who consume diets with low amounts of niacin or folate were found to have reduced arsenicmethylation efficiency.374d Folate supplementation has been found to increase arsenicmethylation efficiency377 and lower blood arsenic levels. People with higher plasma folate levels were found to have decreased risk of urothelial carcinoma378 and skin lesions.379 Diets low in folate were associated with increased chance of arsenic-induced skin lesions.374c Thus a deficiency in B vitamins may increase the toxic effects of arsenic, and exposure to arsenic may increase dietary requirements for B vitamins.374c Smoking is associated with decreased levels of vitamin B12.380 Increased consumption of antioxidants (in particular, vitamins A, C, and E and beta-carotene) reduces skin cancer incidence and arsenic toxicity,90a,272b,297,346h and vitamin E reduces skin cancer risk for mice exposed to nickel and UVR299 and lead toxicity for rabbits exposed to lead.375 Increased consumption of fruits and yellow and light green vegetables was associated with reduced odds of lung cancer in tin miners exposed to arsenic.263 Smoking, both active and passive, has been associated with decreased blood levels of vitamins A, C, iron, zinc, and selenium.381 Vitamin D increases absorption of iron, zinc, and lead.263 Dietary fibre and other dietary constituents Consumption of large quantities of whole grains, with their high phytate and lignin content, can result in zinc deficiency through interfering with zinc absorption, especially if there is low consumption of animal products.261 Thus, diets high in whole grains, legumes, and other sources of dietary fibre and low in animal products may exacerbate adverse health effects from toxic metals by promoting zinc deficiency. Arsenic has been found to decrease absorption of nutrients and has been associated with weight loss;11 thus, consumption of arsenic may promote nutritional deficiencies that increase absorption and adverse effects of other toxic metals. Higher total food and fat intake are associated with decreased lead uptake.263 Dietary deficiencies, malnutrition, and metal toxicity Dietary deficiencies can increase absorption of toxic metals and present shortfalls of antioxidants important for counteracting toxic effects of metals.157 An animal suffering from multiple nutritional deficiencies may be “highly vulnerable” to the toxic effects of heavy metals and nutritional status plays a significant role in determining risk response measures for a given metal.268 Adverse effects of trace elements usually begin to appear at 20 or more times their required intake levels, but with nutrient deficiencies, this may be reduced to only 2 to 3 times the required intake levels.238 Deficiency in methionine, folate, vitamin B12, or selenium decrease arsenicmethylation ability and increase arsenic toxicity,289b,61 while zinc deficiency is associated with decreased ability for DNA repair.261 Iron deficiency increases lead deposition in the bones, and calcium deficiency increases lead and cadmium deposition in kidneys, bones and other tissues.268 Vitamin E deficiency has been shown to increase the toxic effects of lead in rats; concurrent calcium deficiency further amplifies this effect.268 Zinc, iron, folate, vitamin B12, vitamin A, and selenium deficiencies are common throughout the developing world;382 in particular, they are common in regions affected by multiple metal contamination of groundwater (Bangladesh,310,383 India,384 Nepal,385 Cambodia,386 Vietnam;387 Thailand;388 Mongolia389), factors which may be exacerbating the toxic effects of metal exposures. Smokers have been found to have decreased levels of beta-carotene, vitamin C and selenium compared to non-smokers,390 and female smokers and chewers of betel quid in Pakistan were found to have elevated levels of hair and blood cadmium and depressed levels of zinc,391 further increasing risks of metal toxicity for tobacco users in regions with metal-contaminated drinkingwater. Low-level exposures to metals that would otherwise produce at most subtle effects in healthy subjects may produce full-blown toxicity effects in malnourished subjects.208a Malnutrition is associated with increased sensitivity to arsenic toxicity in animals and humans71a,263,374c,d,392 and good nutrition347a,393 and higher BMI90c are associated with reduced incidence of arsenical skin lesions. Children with poor nutritional status had more arsenic lesions and at lower rates of exposure than well-nourished children.394 Increased learning problems are associated with arsenic-exposure in children with chronic malnutrition.395 However, even being well-nourished is not sufficient to prevent the effects of arsenic altogether.83c,206b,263 South Asian diets, environment, cultural factors and metal toxicity Diets in South Asia are heavily based on rice. Regular access to animal protein is limited to people of middle and upper socioeconomic SES,383e and many individuals follow vegetarian diets. Thus, there is relatively high consumption of legumes for protein. Access to fresh fruit is also somewhat limited to people of middle and upper SES.383e Consumption of dairy products is low396 and tea and chilli peppers high. Consumption of fruits and vegetables is lower among South Asian smokers than non-smokers.397 A market basket survey of foods in West Bengal found high levels of arsenic, manganese and nickel, and low levels of zinc.346a Parasitic infestations398 and H. pylori infection399 are not uncommon in South Asia. In much of South Asia, women cover head, arms and legs in public, which reduces sunlight exposure. Periodic fasting is a common and required practice for many communities. These factors are likely to exacerbate the adverse effects of multi-metal exposure. The high consumption of rice adds to the arsenic load, especially if the rice is irrigated with, and then cooked in, arsenic-contaminated water. The high consumption of legumes also adds to the arsenic load, especially when cooked in arsenic-contaminated water. The primarily vegetarian diet is likely to include relatively high amounts of manganese. While the lignins and hemicelluloses in the legumes may decrease the absorption of manganese, they also decrease absorption of zinc. The low consumption of animal products and high consumption of tea and chilli peppers245 increase likelihood of iron deficiency, which further increases absorption of manganese and lead and also increases absorption of cadmium. The low consumption of animal products also increases the likelihood of zinc and selenium deficiencies, a condition made even more serious by the increased need for zinc and selenium under conditions of toxic metal exposure. Parasitic infestations and H. pylori infections further increase the likelihood of zinc and iron deficiencies.216,383d,399 In turn, iron deficiency may increase absorption of lead, chromium and manganese; manganese and lead absorption may also be increased by the low calcium intake of the diets. The general low overall consumption of food may promote higher absorption of lead. While restricting exposure to sunlight may reduce the incidence of arsenic-caused skin lesions, it may also promote vitamin D deficiency, further exacerbating iron and zinc deficiencies. Fasting alters arsenicmethylation processes400 and increases uranium absorption.401 Intake of riboflavin, pyridoxine, vitamin A, vitamin C, calcium and zinc in Bangladesh fall below RDAs for India.297,374c,383e,402 It has been demonstrated that iron deficiency anaemia could be addressed through ferrous sulphate supplementation of drinkingwater,403 but the extent of iron deficiency anaemia in South Asia suggests that although the groundwater in the region often contains high levels of iron, the iron may not be in a bio-available form. Vitamin D levels have been found to be low in Bangladeshi women,404 which may exacerbate arsenic and manganese toxicity by decreasing absorption of iron and zinc. In South Asia, poverty is sometimes measured in terms of calories available for consumption on a daily basis. By this measure, approximately 33–50% of Bangladeshis are “poor”, with fewer than 2122 kilocalories per family member available on a daily basis.405 In Bangladesh, low BMI is associated with poverty and lack of schooling;406 34% of Bangladeshi women have a BMI of less than 18.5.406b In South Asian populations exposed to high levels of arsenic, BMI has been reported to be inversely correlated with incidence of skin lesions.407 BMI has been reported to be lower among tobacco users in India.408 Incidence of underweight is decreasing throughout South Asia, but is still high by world standards;406b,408c,409 one recent study in rural Bangladesh found 56% of children ages 2–6 underweight.383g Effects of multi-metal exposures seem to be more pronounced in undernourished children in Bangladesh.410 It has also been argued that exposure to arsenic may reduce BMI in children.411 If oestrogen does indeed provide some protection from arsenic, then people with decreased oestrogen levels due to low BMI may show increased risk of adverse health effects due to arsenic exposure; this may provide an additional reason for why the poor of South Asia seem particularly susceptible to the effects of arsenic exposure. Research on diet and metal toxicity The dietary factors surrounding individual dietary components and their effects on arsenic toxicity are extremely complex and require further study to disentangle the conflating factors. For instance, an inverse correlation was found between consumption of fruit and canned foods in Bangladesh and incidence of arsenic lesions amongst those exposed to arsenic through drinkingwater.289b However, consumption of fruit and canned foods are more likely with higher SES, and those with higher SES have been shown to be less susceptible to arsenic toxicity,297,412 to have better overall nutritional levels, and higher BMI. Thus, before it can be concluded that consumption of fruit and canned foods can protect against arsenic lesions, the effects of SES and overall good nutrition must be differentiated. Similarly, increased consumption of animal protein was correlated with decreased arsenic toxicity in a Bangladeshi population,346h but consumption of animal protein is also associated with higher SES, possibly reduced consumption of legumes, higher general protein intake, higher general nutrition levels, and higher BMI. Before concluding that animal protein provides a benefit against arsenic toxicity, animal protein consumption must be separated statistically from the other factors, especially legume consumption, since consumption of animal protein in place of legumes implies reduced dietary arsenic exposure, and increased zinc consumption, since zinc is often contained in animal products and may reduce arsenic toxicity. Other exposures to heavy metals Packaging of food products and sweets can be source of significant metal contamination, particularly lead.413 Use of tobacco products implies additional exposure to heavy metals, especially cadmium.209a In addition, pharmaceutical products and vitamins have been found to contain lead,414 manganese,415 or arsenic,416 and herbal remedies have been reported to contain high levels of lead, cadmium, chromium, nickel, manganese, and iron.417 Cosmetics and personal care products, particularly khol or surma, popular in parts of South Asia, may also increase heavy metal exposure.418 Bathing in arsenic-contaminated water can result in elevated urinary arsenic levels.419 It should also be kept in mind that in addition to naturally occurring metals, groundwater may also be further contaminated by toxic metals from mining, industry, or improper disposal of “e-waste”.420 Research on metals and multiple metal effects The only way to tightly control exposure to metals in order to research their health effects is through laboratory studies. However, animal models are often inadequate since they metabolize metals such as arsenic differently than humans and the metals may be more toxic to humans than animals.275b,421 Subtle psychological effects due to metal exposure such as irritability and emotional lability may be difficult to observe in laboratory animals.422 In addition, laboratory studies examining single metal effects can be undermined by inadvertent co-exposure to other metals such as lead, cadmium, or chromium through feed or bedding.104,348 Human epidemiological studies may be the only way to determine the health effects of metal exposures on humans, however, these studies cannot uncover the complete picture if they do not screen for co-exposure to other metals and account for such co-exposures statistically. Even studies that have found a clear link between exposure to a single metal and a direct health effect would benefit from being re-examined in the light of possible multiple metal effects. For example, some authors have reported that the expected correlation between lead exposure in children and neurological symptoms disappeared when co-exposure to other metals was partialed out.83a,208a A variety of toxic metals can cause similar symptoms making it impossible to differentiate metal exposure by the toxic effects that are observed. Where evidence for a direct effect is clear and the biological pathway or mechanism underlying the effect is identified, screening for multiple metal effects would provide additional confirmation that the single metal is indeed the one responsible for the effect. At the same time, multiple metal screening may provide explanation for any observed variation in predicted health effects152 and ultimately lead to a better understanding of the other metals to which subjects may have been exposed. Studies of effects of toxic metals must assume that the possibility of multiple metal exposure is possible, test for multiple metal exposures, and ensure that there is enough variation in population exposure of the studied metals to provide statistical power for factoring the contributions of the various metals alone and in combination. At present, because of lack of research data, US recommended daily allowances (RDAs) and United States Environmental Protection Agency (U.S. E.P.A) reference doses (RfDs for metals do not take into account possible interactions between one trace element and another, even though the normal context of exposure is with multiple elements.423 A common assumption for risk assessment of mixtures is that the effects will be additive, not synergistic. In order for a model to properly predict risk, published research must be available detailing the nature of effects for chemicals in combination (additive, subtractive, or synergistic), but such data are rarely available.424 Some risk assessment models address mixtures of metals, but are limited by the paucity of research that has explored the toxicity of metals in combination.303 A number of alternative approaches to risk assessment with combinations have been proposed.425 Monitoring for biomarkers of oxidative stress may be vital for understanding the effects of chemical mixtures, particularly at low doses.141i Multiple metal effects in children Relatively little epidemiological research has focused on the health effects of metal exposures in children.153,426 It has been argued the risks of drinking metal-contaminated drinkingwater may be different for children than adults427 and that environmental risk exposure for children requires special attention;428 potential reasons for this include children's greater consumption of water per body weight , their rapid development and undeveloped ability to metabolize or excrete toxic metals, the large amount of time spent in their homes where the exposure occurs, their greater likelihood of further exposure through pica and hand-to-mouth activities, and their long life expectancy which may allow time for delayed toxic effects due to early exposures to develop.53,206b,394,429 Periods of rapid mental or physical growth such as infancy or adolescence are also known to increase requirements for essential elements such as zinc,216 making such periods particularly susceptible to trace element deficiencies or metal interactions that reduce availability of trace elements.263 Mice exposed to arsenic only in utero have been shown to have increased risk of cancers as adults;430 in Chile, men exposed to arsenic only as children or adolescents were found to have increased lung cancer mortality as adults.91 Critical periods in development may also be of concern. Infants and children may also be likely to have micronutrient deficiencies that increase absorbance or toxicity of metals they are exposed to; iron deficiency is common among infants and children, and iron deficiency is known to promote uptake of manganese.249a Many researchers have observed that lead, cadmium, and manganese are more toxic to neonates than adults.104,147,308,431 The bioavailability of manganese is greatly increased for infants than adults102,116,128,350 and manganese exposure causes more damage to mice exposed as juveniles than as adults;432 uranium is also absorbed more readily by infant animals50 and uranium is more likely to be deposited in bone with children than with adults.50 In general, prenatal exposure to heavy metals results in adverse health and neurological effects152 and it has been suggested that early exposure to neurotoxic metals may be resulting in a “global pandemic” of neuro-developmental disorders.206b Nevertheless, studies on the health effects of toxic metals have, by design, almost exclusively included only adults, and sometimes only older adults. Epidemiological studies involving children and metals to date have mostly focused solely on learning and intellectual deficits rather than on more general health effects. While the results of the adult health studies are vital for understanding the effects of metal exposure on humans, they do not shed light on any special health risks that may arise when children are exposed to metals. Since no research has been done on the health effects of toxic metals on children, drinkingwater guidelines and RfDs have been calculated solely on the basis of the adult health risk data. While estimates have been made to extend these data to cover children's risks, there has been no research available to confirm whether such extensions provide adequate protection for children;351 it should be noted that adverse effects of manganese exposure in children were found at manganese levels below the Institute of Medicine Upper Level (IOM UL) interpolated from adult risk studies.56a Clinical observations have noted that children seem to develop adverse health effects due to toxic metals before adults given the same level of exposure.2,4,25a,433 In case studies involving single North American families with multiple family members exposed to high levels of metals in private wells, it was the youngest member of each family to show health symptoms, and who became the sickest from the exposure.53,108b,118 Clinical manifestations of arsenic poisoning may not be as obvious with young patients and hence may be overlooked.426b Children may be more sensitive than adults to arsenic-induced toxicity,434 and instances of myocardial infarction, myocardial ischemia, arterial thickening, and other cardiac problems as well as pulmonary effects have been noted in children exposed to arsenic through drinkingwater.11,435 Thus, it is urgent that epidemiological studies be undertaken to develop understanding of the health risks of metal exposure with children. It is also imperative that current drinkingwater guidelines be re-examined in the light of recent research involving learning deficits caused by children's exposure to metals.56,83 Testing for multiple metals in water The storage, preservation, and analysis of drinkingwater samples is complex. This is especially true when these samples are analyzed for more than one analyte. For example, samples collected for boron analyses must be stored in polyethylene containers and cannot be stored in glass containers because glass is both a potential boron source and sink. In contrast, samples collected for total organic carbon analyses must be stored in glass containers and cannot be stored in polyethylene containers because polyethylene is both a potential carbon source and sink. Therefore, the same sample may need to be divided into several different containers at the time of collection.436 The preservation method chosen for a sample is determined by the analytical method and equipment available for analysis. For example, samples collected for arsenic analyses by atomic absorption (AA) spectrometry or inductively coupled plasma mass spectrometry (ICPMS) must be preserved with nitric acid. However, samples collected for arsenic analyses by colorimetric methods such as silver diethyldithiocarbamate cannot be preserved with nitric acid, since oxidizing agents such as nitrate interfere with this method,436 so they must be preserved with hydrochloric acid. In contrast, if a sample is to be analyzed for arsenic by ICPMS, hydrochloric acid must not be used for preservation since the chloride may combine with calcium from the sample matrix to form the polyatomic interference 40Ca35Cl+ at 75 atomic mass units, which is the same mass as the only natural isotope for arsenic, resulting in inflated measured values for arsenic concentration.437 Thus, a sampling plan for drinkingwater that may contain multiple trace and/or toxic elements must be carefully designed, taking into account the special storage and preservation requirements of the different elements as well as potential analytical interferences. Mitigation of contaminated groundwater Alternative sources of drinkingwater In general, it is usually easier and less expensive to find alternative sources of water than treat contaminated water. Possible alternative sources include deeper wells,9a,21a,438 water sharing,438a,439 rain-water harvesting,2,55 or relying on surface water.55,440 Each of these methods may have utility in a given context; however, none is universally available or effective at providing safe water, and risks inherent with the alternative methods must be compared against potential benefits.441 Even where applicable, water from alternative sources must still be tested to ensure that levels of biological pathogens,440 multiple metal contaminants,442 and carcinogenic by-products from treatment443 meet established drinkingwater guidelines. It should be noted that surface water may be additionally contaminated by arsenic-containing irrigation run-off,21a,442b,444 and while deeper wells in Bangladesh and Vietnam may have less arsenic,21a,444,445 deeper wells in China may have more arsenic.446 Drinking water treatment Treatment technologies include both home scale and community systems. A number of low-cost home treatment technologies for arsenic have recently been developed for Bangladesh.447 Arsenic can be removed from drinkingwater using adsorbents.448 In the developed world, home-scale arsenic treatment systems are also available. These vary in cost and effectiveness, but are not regulated by governments.449 Some home-scale treatment technologies are reported to be effective at removing manganese as well as arsenic (e.g. Bangladesh SONO filter447a), however, no independent peer-reviewed data are available concerning the effectiveness of home scale technologies for removing uranium, nickel, or lead. Home treatment systems must also be regularly monitored for bacteriological contamination, particularly in the developing world where chances of such contamination are high.441 An additional concern with home-scale systems is the problem of toxic sludge disposal once the adsorbents have exceeded their utility; it is essential that proper disposal solutions be made, developed and put in place before home-scale treatment systems are adopted for widespread use. Community treatment systems have often been designed to remove a combination of metals, since community water supplies must typically meet multiple drinkingwater guidelines. The most successful community treatment systems are not mass-produced, but rather designed specifically to meet the unique treatment needs of the community. For example, a treatment system in a Greek community was designed to remove arsenic, manganese, and iron, using a combination of biological and chemical treatments.36 One challenge for community-scale water treatment facilities is that maintenance and water quality standards must be rigorously adhered to. Community-scale arsenic treatment facilities in the West Bengal basin do not have a good track record for supplying safe water.450 Recommendations and conclusions Given the severity of adverse health effects caused by potential exposure to metals in groundwater it is vital for governments to increase their understanding of the specific risks faced by their populations and how these risks can be avoided. Systematic national water testing surveys based on stratified random sampling should be undertaken to test groundwater for multiple elements, including especially those known to commonly appear in groundwater that have recognized toxic effects: arsenic, manganese, fluoride, uranium, lead, and nickel. Laws must also be promulgated requiring testing of public water supplies and governments must ensure that the laws are followed. These laws need to be re-examined regularly and updated to take into consideration continuing research on the toxicity of single and multiple metals. Stakeholders must be educated about the need for testing of private wells, putting special emphasis on the need for testing in areas identified as possible “hot spots” of contamination by national surveys. The reliability of drinkingwater test results must be ensured by monitoring and regulating private water testing laboratories. Governments may find it cost-effective to subsidize water testing for private wells. In terms of public health, it is less expensive to help populations avoid exposure to toxic metals than to treat any resulting diseases or provide support for families if disability or death occurs as a result of exposure. For too many people worldwide, drinkingwater contains biological pathogens, carcinogenic treatment residues, or toxic metals. A variety of factors are pushing populations to rely on groundwater, including increased access to well technology, improved understanding of biological pathogens in surface water, increasing population pressures, migration to decentralized areas, political upheavals, and global climate change. Whenever a new source of water is accessed, particularly groundwater, it is crucial for public health that the water be tested for the presence of multiple metals as well as biological pathogens. It must be kept in mind that multiple metal exposure is the natural form of environmental metal exposure. 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She has been a part of an international team of volunteer scientists in Bangladesh since 1998, mapping the extent of arsenic and other toxic metals in the groundwater and developing methods for groundwater testing. She has strong interests in societal factors involving diet and nutrition, and societal responses to proposed technological solutions for groundwater remediation. Open in new tabDownload slide Dr Seth H. Frisbie is an environmental and analytical chemist at Norwich University, and the president of a nonprofit corporation, Better Life Laboratories, Inc. He received his doctoral and master's degrees from Cornell University. He has studied drinking water for over 30 years. He has worked on drinking water and public health in Bangladesh and other developing countries since 1997. Open in new tabDownload slide Bibudhendra Sarkar received his PhD in biochemistry from the University of Southern California and did his further studies in protein chemistry in Cambridge University and quantum biochemistry in the Université de Paris-Sorbonne. At the University of Toronto and the Hospital for Sick Children, he established his research career in metal-caused diseases. He became full professor in 1978, department head of Structural Biology and Biochemistry 1990–2002 and director of the Advanced Protein Technology Center 1998–2002. Since 1997 he has been leading a team of international volunteer scientists researching the health crisis caused by multiple metals contamination of drinking water in South Asia. Erika Mitchell and Seth Frisbie are members of this team. © The Royal Society of Chemistry 2011 This article is published and distributed under the terms of the Oxford University Press, Standard Journals Publication Model (https://academic.oup.com/journals/pages/open_access/funder_policies/chorus/standard_publication_model) © The Royal Society of Chemistry 2011 TI - Exposure to multiple metals from groundwater—a global crisis: Geology, climate change, health effects, testing, and mitigation JF - Metallomics DO - 10.1039/c1mt00052g DA - 2011-08-30 UR - https://www.deepdyve.com/lp/oxford-university-press/exposure-to-multiple-metals-from-groundwater-a-global-crisis-geology-LfM0RF5m0f SP - 874 EP - 908 VL - 3 IS - 9 DP - DeepDyve ER -