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CAS N020

Arsenic compounds

heavy metalcarcinogenHAPSDWAOSHA carcinogen

Arsenic compounds — encompassing inorganic arsenic in groundwater, organic arsenicals in pesticides, and arsenic trioxide in industry — constitute the most widespread naturally occurring human carcinogen, affecting over 200 million people globally through contaminated drinking water while simultaneously providing one of medicine's oldest and most dramatic cancer treatments.

Where It Comes From

Arsenic has been used as both poison and medicine for millennia — in 18th-century Europe, arsenic trioxide was a fashionable poison, and Fowler's Solution (1% potassium arsenite) was prescribed for a century as a tonic and cancer treatment [1]. The modern crisis is geological rather than industrial: in Bangladesh and West Bengal, India, aquifer sediments release inorganic arsenic (arsenite, As III; arsenate, As V) into groundwater that tens of millions of people drink daily [2]. This geological catastrophe — arguably the largest mass poisoning in human history — was ironically triggered by a well-intentioned public health campaign in the 1970s that drove people from cholera-contaminated surface water to 'safe' groundwater without testing for arsenic. Similar geogenic contamination affects parts of Chile, Argentina, Taiwan, Mexico, and the western United States. Industrial arsenic compounds come from copper and gold smelting (arsenic is a byproduct of sulfide ore processing), wood preservative CCA (chromated copper arsenate, used in pressure-treated lumber until 2003), herbicides (monosodium methyl arsenate, MSMA), and glass manufacturing [1].

How You Are Exposed

The primary pathway globally is drinking water from arsenic-contaminated wells, most severely in South and Southeast Asia, Latin America, and parts of the United States [1]. In the U.S., parts of New England, the Great Plains, and the Southwest have naturally elevated groundwater arsenic — private well users are not covered by the EPA 10 µg/L drinking water standard and must test their own wells [2]. Dietary intake is significant: rice and rice-based products (rice milk, rice cereal, brown rice) accumulate inorganic arsenic from soil and irrigation water — brown rice has 80% more arsenic than white rice [1]. Seafood contains arsenobetaine and organic arsenicals generally considered less toxic. Workers in copper smelting, pesticide production, and wood treatment face occupational inhalation [2]. Children are exposed through soil contact near former orchards (where lead arsenate pesticide was historically used) and CCA-treated wooden playground equipment [1].

Why It Matters

Inorganic arsenic is metabolized by methylation (As III → MMA III → DMA V) in the liver, but the intermediate MMA(III) is more reactive and toxic than the parent compound [1]. Arsenic inhibits key enzymes in the pyruvate dehydrogenase complex and the citric acid cycle, disrupting cellular energy production. It generates reactive oxygen species, causes DNA strand breaks, inhibits DNA repair, and disrupts telomerase function — explaining its multi-organ carcinogenicity [2]. IARC classifies inorganic arsenic as a Group 1 carcinogen for bladder, lung, and skin cancers; associations with kidney, prostate, and liver cancer are also documented [1]. Chronic arsenic also causes characteristic skin lesions (keratosis, hyperpigmentation, 'raindrop' depigmentation), peripheral neuropathy, and cardiovascular disease at lower doses than cancer [2].

Who Is at Risk

Private well users in arsenic-endemic regions of the U.S. (New England bedrock aquifers, Great Plains alluvial deposits, Southwest volcanic deposits) are a major at-risk group [1]. Infants and young children fed rice cereal or rice milk have disproportionately high dietary arsenic per body weight. Workers in copper, gold, and lead smelting; pesticide manufacturing; and glass production face occupational inhalation exposure [2]. In South Asia, 200+ million people drink water exceeding the WHO guideline of 10 µg/L. Individuals who are poor methylators (those lacking MTHFR capacity or those with inadequate folate) metabolize arsenic to more toxic intermediates [1].

How to Lower Your Exposure

1. Test your private well annually for arsenic — contact your state health department or use an NSF-certified lab; many New England and western states have high bedrock arsenic [1]. 2. Use a certified reverse osmosis filter for drinking and cooking water if your arsenic exceeds 10 µg/L [2]. 3. Diversify grain intake — replace some rice with quinoa, oats, or other grains, and don't feed infants exclusively rice cereal [1]. 4. Cook rice in a large volume of water (6:1 water:rice ratio) and drain — this reduces inorganic arsenic by up to 57% [2]. 5. Avoid old CCA-treated wood playgrounds, and seal existing CCA-treated wood decks with penetrating sealant every year or two [1]. 6. If occupationally exposed in smelting or pesticide production, use appropriate respiratory protection and biological monitoring programs [2].

References

  1. [1]IARC (2012). Monographs Volume 100C: Arsenic and Arsenic Compounds. https://monographs.iarc.fr/
  2. [2]Naujokas MF et al. (2013). The broad scope of health effects from chronic arsenic exposure. Environmental Health Perspectives. https://doi.org/10.1289/ehp.1204994

Recovery & Clinical Information

Body Half-Life

Inorganic arsenic has a blood half-life of approximately 1-4 days; urinary arsenical metabolites clear within 1-2 weeks of stopping acute exposure [1]. However, arsenic accumulates in hair and nails (keratin-bound), where it persists for months — these are historical exposure biomarkers rather than current-dose indicators [2]. Chronic low-level exposure from drinking water results in slow accumulation in skin, nails, and hair.

Testing & Biomarkers

First-morning urine arsenic (speciated — inorganic + methylated arsenicals, excluding arsenobetaine) by ICP-MS is the preferred biomarker for exposure assessment [1]. Total urine arsenic is unreliable because high seafood intake inflates values with non-toxic organic arsenicals. Hair arsenic (segment analysis) for retrospective timeline reconstruction [2]. Serum arsenic for acute high-level exposures [1]. Request speciated urine arsenic from occupational health or environmental medicine labs.

Interventions

Source elimination is the top priority — replace the contaminated water supply or install point-of-use reverse osmosis filtration [1]. DMSA (succimer) chelation is used for acute high-level arsenic poisoning; BAL (dimercaprol) for severe acute toxicity [2]. Folate and selenium may improve arsenic methylation efficiency, potentially reducing formation of the most toxic intermediates [1]. Selenium is particularly important — it forms inactive complexes with arsenic [2].

Recovery Timeline

Urine arsenic normalizes within 2 weeks of source elimination [1]. Skin lesions (keratosis) may slowly improve over months to years after stopping chronic exposure but may not fully resolve [2]. Cancer risk from past arsenic exposure does not return to baseline for bladder and skin cancers, but reducing ongoing exposure prevents further risk accumulation [1].

Recovery References

  1. [1]ATSDR (2007). Toxicological Profile for Arsenic. https://www.atsdr.cdc.gov/toxprofiles/tp2.pdf
  2. [2]EPA (2023). Arsenic in Drinking Water. https://www.epa.gov/ground-water-and-drinking-water/national-primary-drinking-water-regulations

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