Skip to content
Heavy Metal Index

A mass-balance model to assess arsenic exposure from multiple wells in Bangladesh

Source

Using a mass-balance model applied to the Health Effects of Arsenic Longitudinal Study (HEALS) cohort of 11,197 participants in Araihazar, Bangladesh, Huhmann and colleagues show that participants on average obtain 60–75% of their drinking water from their primary household well and 25–40% ...

Page snapshot
Cited by4 pages
Metals measured1
Evidence tierA
Year2022

Overview

Using a mass-balance model applied to the Health Effects of Arsenic Longitudinal Study (HEALS) cohort of 11,197 participants in Araihazar, Bangladesh, Huhmann and colleagues show that participants on average obtain 60–75% of their drinking water from their primary household well and 25–40% from other wells, correcting a systematic underestimate in prior exposure assessments that relied solely on the primary well. Their new rice arsenic measurements (n=814 samples from 410 HEALS households) indicate that rice rather than drinking water is the largest As exposure source for participants whose primary wells contain 50 µg/L or less of As.

Key numbers

HEALS cohort: 11,197 participants, Araihazar, Bangladesh, baseline 2000–2002. Linear regression of urinary As on primary-well As: slope 0.69 ± 0.01, intercept 68 ± 2. Primary well As: study area mean 95 µg/L. Mass-balance model estimates fraction of drinking water from primary well: fp = 0.50 ± 0.08 (using local rice As estimate); fraction from other wells: ~0.18 ± 0.08; fraction from food and cellular respiration accounts for the remainder. Estimated daily As intake from rice: 96 µg/day (local rice estimate) or 64 µg/day (previously published El-Masri estimate). Rice arsenic (total As, ICP-MS or HPLC-ICP-MS): uncooked rice mean 244 ± 150 µg/kg, cooked rice mean 235 ± 180 µg/kg (n=408 uncooked, 406 cooked). Range: 50–1,200 µg/kg total As. Certified reference standard SRM 1568b: measured 312±10 µg/kg (ICP-MS) and 325±18 µg/kg (HPLC-ICP-MS) against certified 285±14 µg/kg.

Methods (brief)

Well-water As measured by blanket survey (2000–2002) across 25 km² study area. Urinary As collected at baseline. Rice samples collected 2016 from subset of 410 HEALS households; microwave digestion followed by ICP-MS (total As) or HPLC-ICP-MS (speciated As). The paper reports total As only for rice; speciation not differentiated in the reported rice values. Study design is observational cohort; mass-balance model uses linear regression.

Implications

Certification: Rice As values (50–1,200 µg/kg tAs, mean ~240 µg/kg) from Bangladeshi households represent a high-contamination scenario; relevant to the app model for populations with high rice consumption and for HMT&C threshold context in international markets. The finding that rice displaces drinking water as the dominant As source at lower well-water concentrations is relevant to aggregate dietary exposure modeling.

Courses: Illustrates that single-source exposure assessment systematically underestimates As burden; important for teaching exposure pathway complexity.

App: Bangladesh rice samples provide distributional data for a high-tAs rice scenario; mean 240 µg/kg and range 50–1,200 µg/kg (total As). iAs/tAs ratio not directly reported; do not assume these values represent iAs alone.

Wiki pages updated on ingest

Update history

The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and the full version history lives in git. When DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.

CommitDateChangeDescription
e3171892026-08-11correction6 sections added; narrative text revised