4.7 Article

Arsenic in drinking water, hair, and prevalence of arsenicosis in Perak, Malaysia

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FRONTIERS IN PUBLIC HEALTH
卷 11, 期 -, 页码 -

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FRONTIERS MEDIA SA
DOI: 10.3389/fpubh.2023.998511

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arsenic poisoning; hair; water; prevalence; carcinogens; mass spectrometry

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A comparative cross-sectional study was conducted in two villages in Malaysia to assess the prevalence of arsenicosis and determine the arsenic concentrations in drinking water and hair. The results showed that 41% of water samples from one village exceeded the safe level of arsenic, while none of the samples from the other village did. Additionally, 13.5% of the respondents had arsenic levels above the safe limit in their hair. Factors such as living in the high arsenic village, being female, increasing age, and smoking were significantly associated with higher arsenic levels in hair. Immediate mitigation actions are needed to reduce the risk of arsenicosis in the exposed village.
Arsenic is a carcinogen element that occurs naturally in our environment. Humans can be exposed to arsenic through ingestion, inhalation, and dermal absorption. However, the most significant exposure pathway is via oral ingestion. Therefore, a comparative cross-sectional study was conducted to determine the local arsenic concentration in drinking water and hair. Then, the prevalence of arsenicosis was evaluated to assess the presence of the disease in the community. The study was conducted in two villages, namely Village AG and Village P, in Perak, Malaysia. Socio-demographic data, water consumption patterns, medical history, and signs and symptoms of arsenic poisoning were obtained using questionnaires. In addition, physical examinations by medical doctors were performed to confirm the signs reported by the respondents. A total of 395 drinking water samples and 639 hair samples were collected from both villages. The samples were analyzed using Inductively Coupled Plasma-Mass Spectrometry (ICP-MS) to determine arsenic concentration. The results showed that 41% of water samples from Village AG contained arsenic concentrations of more than 0.01 mg/L. In contrast, none of the water samples from Village P exceeded this level. Whilst, for hair samples, 85 (13.5%) of total respondents had arsenic levels above 1 mu g/g. A total of 18 respondents in Village AG had at least one sign of arsenicosis and hair arsenic levels of more than 1 mu g/g. Factors significantly associated with increased arsenic levels in hair were female, increasing age, living in Village AG and smoking. The prevalence of arsenicosis in the exposed village indicates chronic arsenic exposure, and immediate mitigation action needs to be taken to ensure the wellbeing of the residents in the exposed village.

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