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Management of People Exposed to Drinking Water with Excessive Heavy Metals Training to PCD 2017
Antimony (Sb): Important sources of human exposure • Significant antimony exposures may occur in an
occupational setting including metal smelting, coal-fired power plants and refuse incineration.
• Antimony compound (at a dosage of 20,000 µg/kg/day) has been used in the treatment of some parasitic infection
• Total exposure from food and drinking-water is relatively very low compared with the conditions above
Sb: guideline values • WHO drinking water guideline value for Antimony: 20 μg/L
• WHO Tolerable daily intake (TDI): 6 μg/kg body weight (360 μg/day for a 60kg person)
Toxicities of Sb after oral exposure
• Oral intake of soluble antimony salts (at the level of 30,000 – 60,000 µg) may exert a strong irritating effect on the gut and trigger sustained vomiting
• Reported toxicities after oral exposure are mainly due to ingestion of soluble Sb3+ salts • Acute
• Mainly gastrointestinal (vomiting, diarrhea, abdominal cramps) • Cardiotoxicity • Similar to Arsenic
• Chronic • Oculotoxicity (optic neuropathy, uveitis, retinal bleeding)
[WHO] [Agency for Toxic Substances and Disease Registry (ATSDR), CDC] Handbook of the Toxicology of Metals, 3rd edition
Toxicities of Sb after oral exposure
• No acute/chronic systemic toxicities after oral exposure to Sb5+ were reported from the literature • For therapeutic exposure to parenteral Sb5+ drugs, acute/subacute and
rarely chronic toxicities (gastrointestinal, cardiovascular, pancreatitis, hepatotoxicity) were reported, usually not severe and reversible
• No reproductive/developmental toxicities were reported after
oral exposure to Sb
• No evidence to indicate carcinogenicity by the oral route
[WHO] [Agency for Toxic Substances and Disease Registry (ATSDR), CDC]
Therapeutic Vs toxic dosages of Sb5+
• WHO guideline water Sb level: 20 ug/L • Recommended therapeutic dose of Sb5+
• 20 mg/kg/day with no upper limit [Am J Trop Med Hyg.1992 Mar;46(3):296-306.][WHO]
• By IM or IV injection • For a average 50-kg person therapeutic dose = 1 g/day Even if the water Sb level is 10x the WHO recommended control
level (200 ug/L) one has to drink 50,000 L of water to be equivalent to that for therapeutic use (assuming all Sb5+ can be absorbed after ingestion)
Cadmium (Cd) • No known biological role for Cd or its salts
• Undetectable at birth • Bioaccumulation appears to be a by-product of increasing
industrialization
• Major sources:
• From non-ferrous metal mining and refining, manufacture and application of phosphate fertilizers, fossil fuel combustion, waste incineration and disposal
• Under non-occupational settings, food is the main source of exposure to cadmium. According to WHO, dietary daily intake of individuals ranges from 10 to 35 μg.
• Smoking will increase the intake of cadmium
Cd: guideline values
• WHO drinking water guideline value for Cadmium: 3 μg/L
• WHO Provisional tolerable monthly intake (PTMI) = 25 μg/kg body weight (equivalent to about 50 μg/day for a 60kg person)
Cadmium toxicities after oral exposure • Acute excessive ingestion, mainly gastrointestinal (GI) effect:
– Lethal oral dose: 350-3500 mg • A dose of 3 mg Cd (i.e. 1000 L water at WHO Cd cutoff or 100 L at 10x
WHO Cd cutoff) has no acute effects on adults (Krajnc et al., 1987) – GI effects: Nausea, vomiting, diarrhea, abdominal pain, tenesmus – Rarely: hemorrhagic gastroenteritis, liver and kidney necrosis, cardiomyopathy,
metabolic acidosis
• Chronic toxicities, mainly renal effect: – Renal: Progressive renal tubular dysfunction, proteinuria, nephrolithiasis
• Chronic intake 140 - 255 ug Cd per day (drink 2 litres of water per day at 20x – 40x of WHO Cd guideline value) associated with low molecular weight proteinuria in elderly (JECFA, 1989)
– Musculoskeletal: Bone lesions secondary to Cd-induced renal damage and cadmium accumulates in bone
• pseudofracture, osteomalacia, osteoporosis
• Chronic toxicities (con’t): – Carcinogenicity: IARC as group 1 carcinogen
• Carcinogenicity well demonstrated in experimental animals, less conclusive in humans (other than strongest evidence with inhalational exposure in occupational setting and lung cancer)
– Specific groups:
• Pregnancy: inconsistent evidence about its effect on pregnancy, may increase incidence of preterm delivery; anyway, not known to be teratogenic
• Lactating: small amount will enter breast milk (5-10% of level in blood)
• Children: Similar health effect as adult, no definite harmful effects on child development or behavior have been reported.
Cadmium toxicities after oral exposure
Chromium (Cr) Trivalent form (Cr3+) Hexavalent form (Cr6+)
• Essential trace element important in glucose metabolism
• Deficiency associated with diabetes and atherosclerosis
• Form of Cr given as IV/oral supplement if indicated
• Little evidence that Cr3+ is toxic or carcinogenicity to human
• IARC: Not classifiable as carcinogen in human
• High oxidative potential at point of entrance, causes damage to cellular constituents, hence considered genotoxic, cytotoxic and carcinogenic
• Toxicological importance in inhalational occupational exposure with major risk of carcinogenesis e.g. bronchogenic/ nasal
• IARC: Known human carcinogen by inhalation route only
[Tietz. 5e] [Goldfrank 10e]
Chromium: oral exposure
• Water • Leaching from distribution system in both Cr3+ and Cr6+
[Shock et al., 2008]
• Food - Present in meat, fish, fruit, vegetable
• All present as Cr3+ unless contaminated by local source [Sanexen, 2009]
• Under non-occupational settings, food remains the major source of chromium intake. WHO report indicated that food contributes 93–98% of the total intake of chromium while 1.9–7% from water.
[Chromium in Drinking-water, WHO 2003] [Goldfrank. 10e][Tietz. 5e]
Cr: guideline value • WHO drinking water provisional guideline value for
Chromium: 50 μg/L
Chronic dietary exposure to Cr6+
• Carcinogenesis
• Limited data on carcinogenesis from oral exposure in human
• Increase GI tract neoplasms on chronic oral exposure in animal study
• Adverse effects of using of water with exceedingly high Cr6+ level has once been reported in China [Zhang and Li, 1987] • [Cr6+] in drinking water 20,000 µg/L (400X WHO cutoff for total Cr)
• 155 subjects developed sores in the mouth, diarrhea, stomachache, indigestion, vomiting, elevated white blood cell counts with respect to controls, and a higher per capita rate of cancers, including lung cancer and stomach cancer
• Note: Precise exposure concentrations, exposure durations, and confounding factors were not discussed
[WHO] [Agency for Toxic Substances and Disease Registry (ATSDR), CDC]
Chronic dietary exposure to Cr6+
• Non-cancer effects • Reproductive/ Developmental
• Limited reports in human (by ingestion route) • Decrease sperm count, increase % abnormal sperm observed in
animals (≥5200 µg/kg/day) • Post-implantation loss, decreased fetal weight, internal and skeletal
malformation in animals (≥ 35,000 µg/kg/day)
• Others (with much higher level of exposure) • Haematological (microcytic, hypochromic anaemia) • Mild to moderate elevation in hepatic aminotransferases and
abnormal liver architecture • Transient elevation in urinary ß-microglobulin
[WHO] [Agency for Toxic Substances and Disease Registry (ATSDR), CDC]
Cu: Common Sources • Copper is an essential element that has regulated GI
absorption
• Food is the most common source. Dietary copper intakes for adults range from 1 to 3 mg/day in some studies.
• Copper is an essential trace element.
• Drinking water contributes 0.1–1 mg/day in most situations.
• Use of vitamin/mineral supplement will increase exposure by up to 2 mg/day
Cu: guideline value
• WHO drinking water guideline value for Copper: 2 mg/L
• WHO upper safe limit for copper consumption is estimated to be 10 mg/day
Toxicities of Cu after oral exposure • Acute
• GI irritation (at 4-8 mg/L) with rapid onset vomiting, abdominal pain and less commonly GI bleeding or even perforation. Metallic taste and retrosternal chest pain.
• Rapid haemolysis following methaemoglobinaemia • Systemic effects include hepatotoxicity, renal and lung toxicities
occasionally. • Most severe cases may lead to shock, CNS depression and sepsis.
• Chronic
• Implication in pathogenesis of neurodegenerative diseases e.g. Alzheimer and Parkinson
Cu: Sensitive Population • Children and infants, especially with infant formula
reconstituted with tap water • higher absorption and lower excretion
• Genetic defects in copper metabolism:
• Wilson disease (prevalence 1 in 5400 in Hong Kong [Mak]) • Restriction of dietary copper alone cannot influence the
progression of the disease [WHO] • Chelation: d-penicillamine, trientine • Liver transplant improves CNS symptoms
Nickel (Ni): Common Sources • Food is the dominant source of nickel exposure in the non-
smoking, non-occupationally exposed population • Oatmeal, dried beans, leaching from nickel containing food
processor
• Water is generally a minor contributor to the total daily oral intake of nickel
Ni: guideline values • WHO drinking water guideline value for Nickel: 70 μg/L
• WHO Tolerable daily intake (TDI) = 12 μg/kg body weight (720 μg/day for a 60kg person)
Toxicities of Ni ingestion
• Dermatological • Eczematous flare-up reactions in skin (Ni-sensitive individuals) • Generalised dermatitis in a 2 year-old boy swallowed two coins
• Carcinogenicity
• Nickel compounds (e.g., Ni oxides, sulphides) are classified as class I carcinogen; metallic nickel are 2B (possibly carcinogenic to humans)
• Inhaled nickel compounds are carcinogenic to humans but there is a lack of evidence of a similar risk from oral ingestion of nickel
Summary • The WHO defined drinking water limits for the five metals
are stringent and substantially lower than the levels causing clinical poisoning
• Universal screening for these metals in blood and urine samples for subjects exposed to drinking water with mildly elevated levels will not be helpful in identifying poisoning
• Such practice is not seen in the rest of the world
• Reduction of exposure by avoidance of such water is the primary measure in clinical management