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Identification of key factors and mechanism determining arsenic mobilization in paddy soil-porewater-rice system.
Kong, Shuqiong; Cai, Dawei; Shao, Yixian; Wei, Xiaguo; Yi, Zhihao; Root, Robert A; Chorover, Jon.
Afiliación
  • Kong S; MOE Key Laboratory of Groundwater Quality and Health, China University of Geosciences, Wuhan, Hubei 430078, China; School of Environmental Studies, China University of Geosciences, Wuhan, Hubei 430078, China. Electronic address: ksq@cug.edu.cn.
  • Cai D; College of Environmental Sciences and Engineering, Peking University, Beijing 100871, China.
  • Shao Y; Zhejiang Institute of Geological Survey, Hangzhou, Zhejiang 311200, China.
  • Wei X; MOE Key Laboratory of Groundwater Quality and Health, China University of Geosciences, Wuhan, Hubei 430078, China; School of Environmental Studies, China University of Geosciences, Wuhan, Hubei 430078, China.
  • Yi Z; MOE Key Laboratory of Groundwater Quality and Health, China University of Geosciences, Wuhan, Hubei 430078, China; School of Environmental Studies, China University of Geosciences, Wuhan, Hubei 430078, China.
  • Root RA; Department of Environmental Science, University of Arizona, Tucson, AZ 85721, United States. Electronic address: rroot@email.arizona.edu.
  • Chorover J; Department of Environmental Science, University of Arizona, Tucson, AZ 85721, United States. Electronic address: chorover@arizona.edu.
J Hazard Mater ; 479: 135684, 2024 Nov 05.
Article en En | MEDLINE | ID: mdl-39241359
ABSTRACT
Arsenic (As) mobilization in paddy fields poses significant health risks, necessitating a thorough understanding of the controlling factors and mechanisms to safeguard human health. We conducted a comprehensive investigation of the soil-porewater-rice system throughout the rice life cycle, focusing on monitoring arsenic distribution and porewater characteristics in typical paddy field plots. Soil pH ranged from 4.79 to 7.98, while porewater pH was weakly alkaline, varying from 7.2 to 7.47. Total arsenic content in paddy soils ranged from 6.8 to 17.2 mg/kg, with arsenic concentrations in porewater during rice growth ranging from 2.97 to 14.85 µg/L. Specifically, arsenite concentrations in porewater ranged from 0.48 to 7.91 µg/L, and arsenate concentrations ranged from 0.73 to 5.83 µg/L. Through principal component analysis (PCA) and analysis of redox factors, we identified that arsenic concentration in porewater is predominantly influenced by the interplay of reduction and desorption processes, contributing 43.5 % collectively. Specifically, the reductive dissolution of iron oxides associated with organic carbon accounted for 23.3 % of arsenic concentration dynamics in porewater. Additionally, arsenic release from the soil followed a sequence starting with nitrate reduction, followed by ferric ion reduction, and subsequently sulfate reduction. Our findings provide valuable insights into the mechanisms governing arsenic mobilization within the paddy soil-porewater-rice system. These insights could inform strategies for irrigation management aimed at mitigating arsenic toxicity and associated health risks.
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Texto completo: 1 Colección: 01-internacional Base de datos: MEDLINE Asunto principal: Arsénico / Oryza / Contaminantes del Suelo / Contaminantes Químicos del Agua Idioma: En Revista: J Hazard Mater Asunto de la revista: SAUDE AMBIENTAL Año: 2024 Tipo del documento: Article Pais de publicación: Países Bajos

Texto completo: 1 Colección: 01-internacional Base de datos: MEDLINE Asunto principal: Arsénico / Oryza / Contaminantes del Suelo / Contaminantes Químicos del Agua Idioma: En Revista: J Hazard Mater Asunto de la revista: SAUDE AMBIENTAL Año: 2024 Tipo del documento: Article Pais de publicación: Países Bajos