Key facts

Contaminant group
Metal
World Health Organization — guideline
10 µg/l
Provisional, set by measurement and treatment feasibility rather than by an acceptable risk level.
European Union — legal limit
10 µg/l
United Kingdom — legal limit
10 µg/l
United States — legal limit
10 µg/l
Lowered from 50 µg/l in 2001.
Bangladesh — legal limit
50 µg/l
A higher national standard than the WHO guideline, reflecting the scale of the contamination and the practical limits of remediation.

Where it comes from

  • Natural dissolution from arsenic-bearing sediments and volcanic rock — by far the dominant source globally
  • Mining and smelting waste
  • Historic arsenical pesticides and wood preservatives
  • Geothermal water

How it behaves in water

Mobility depends on redox conditions and pH. Arsenite (As III) dominates in reducing groundwater and is both more toxic and harder to remove than arsenate (As V), which dominates in oxidising conditions. Effective treatment usually begins by oxidising As III to As V.

How it is measured

Measured in micrograms per litre, usually by ICP-MS. Field test kits exist and were widely used in the Bangladesh well-screening programmes, but have poor precision near the limit.

Regulatory position

Regulatory values for arsenic
JurisdictionValueStatusNotes
World Health Organization10 µg/lguidelineProvisional, set by measurement and treatment feasibility rather than by an acceptable risk level.
European Union10 µg/llegal limit
United Kingdom10 µg/llegal limit
United States10 µg/llegal limitLowered from 50 µg/l in 2001.
Bangladesh50 µg/llegal limitA higher national standard than the WHO guideline, reflecting the scale of the contamination and the practical limits of remediation.

Table sources

Health context

Long-term ingestion causes skin lesions, and is causally associated with cancers of the skin, bladder and lung. IARC classifies arsenic and inorganic arsenic compounds in Group 1. Effects arise from chronic exposure over years, not from single exposures.

What removes it

Treatment effectiveness
RowEffectiveNot reliably effective
1Coagulation with iron salts followed by filtrationBoiling, which concentrates it
2Adsorption onto iron oxide or activated alumina mediaActivated carbon alone
3Reverse osmosisSediment filtration
4Ion exchange, for arsenateConventional chlorination without a removal step
5Oxidation to As V before any of the above

Occurrence

The affected populations are concentrated where deep tube wells were installed to escape microbially contaminated surface water — a case where solving one water problem created another.

Relationships

    Related intelligence

    Sources