4.7 Article

Evaluation of a water arsenic filter in a participatory intervention to reduce arsenic exposure in American Indian communities: The Strong Heart Water Study

Journal

SCIENCE OF THE TOTAL ENVIRONMENT
Volume 862, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.scitotenv.2022.160217

Keywords

Arsenic; Private wells; Community-driven research; DRINKING WATER; Mitigation

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Many rural populations, including American Indian communities, are disproportionately exposed to elevated levels of arsenic in their private well water. The Strong Heart Water Study aimed to reduce arsenic exposure among private well users in American Indian Northern Great Plains communities. The study found that the installation of point-of-use arsenic filters and the delivery of health communication programs were effective in reducing water arsenic concentration in study households over a two-year period.
Many rural populations, including American Indian communities, that use private wells from groundwater for their source of drinking and cooking water are disproportionately exposed to elevated levels of arsenic. However, programs aimed at reducing arsenic in American Indian communities are limited. The Strong Heart Water Study (SHWS) is a ran-domized controlled trial aimed at reducing arsenic exposure among private well users in American Indian Northern Great Plains communities. The community-led SHWS program installed point-of-use (POU) arsenic filters in the kitchen sink of households, and health promoters delivered arsenic health communication programs. In this study we evaluated the efficacy of these POU arsenic filters in removing arsenic during the two-year installation period. Par-ticipants were randomized into two arms. In the first arm households received a POU arsenic filter, and 3 calls promot-ing filter use (SHWS mobile health (mHealth) & filter arm). The second arm received the same filter and phone calls, and 3 in-person home visits and 3 Facebook messages (SHWS intensive arm) for program delivery. Temporal variability in water arsenic concentrations from the main kitchen faucet was also evaluated. A total of 283 water sam-ples were collected from 50 households with private wells from groundwater (139 filter and 144 kitchen faucet sam-ples). Ninety-three percent of households followed after baseline had filter faucet water arsenic concentrations below the arsenic maximum contaminant level of 10 mu g/L at the final visit during our 2 year study period with no difference between study arms (98 % in the intensive arm vs. 94 % in the mHealth & filter arm). No significant temporal variation in kitchen arsenic concentration was observed over the study period (intraclass correlation coefficient = 0.99). This study demonstrates that POU arsenic filters installed for the community participatory SHWS program were effective in reducing water arsenic concentration in study households in both arms, even with delivery of the POU arsenic filter and mHealth program only. Furthermore, we observed limited temporal variability of water arsenic concentrations from kitchen faucet samples collected over time from private wells in our study setting.

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