Biochar affects methylmercury production and bioaccumulation in paddy soils: Insights from soil-derived dissolved organic matter

• Published in: Journal of environmental sciences (China) Vol. 119; pp. 68 - 77
• Main Authors: Zhang, Siqi, Wang, Mingxing, Liu, Jiang, Tian, Shanyi, Yang, Xueling, Xiao, Guangquan, Xu, Guomin, Jiang, Tao, Wang, Dingyong
• Format: Journal Article
• Language: English
• Published: Elsevier B.V 01.09.2022
• Subjects: Biochar; Dissolved organic matter; Mercury; Methylmercury; Rice; Dissolved organic matter; Biochar; Mercury; Methylmercury; Rice
• ISSN: 1001-0742; 1878-7320
• DOI: 10.1016/j.jes.2022.02.011

•Biochar significantly changes the nature of dissolved organic matter (DOM) in soil.•Biochar addition increases the aromaticity and molecular weight of soil DOM.•Modified biochar can effectively reduce the methylation rate in paddy soil.•Biochar significantly decreases MeHg bioaccumulation in rice plants, especially in grain.•Soil DOM modified by biochar is vital to the fate of mercury in rice field. Biochar has been used increasingly as a soil additive to control mercury (Hg) pollution in paddy rice fields. As the most active component of soil organic matter, soil dissolved organic matter (DOM) plays a vital role in the environmental fate of contaminants. However, there are very few studies to determine the impact of biochar on the Hg cycle in rice paddies using insights from DOM. This study used original and modified biochar to investigate their effect on DOM dynamics and their potential impact on methylmercury (MeHg) production and bioaccumulation in rice plants. Porewater DOM was collected to analyze the variations in soil-derived DOM in paddy soils. The results showed that the addition of biochar, whether in original or modified form, significantly reduced the bioaccumulation of MeHg in rice plants, especially in hulls and grains (p<0.05). However, MeHg production in soils was only inhibited by the modified biochar. Biochar addition induced a significant increase in DOM's aromaticity and molecular weight (p<0.05), which decreased Hg bioavailability. Furthermore, enhanced microbial activity was also observed in DOM (p<0.05), further increasing MeHg production in the soil. Thus, the effect of biochar on the fate of Hg cycle involves competition between the two different roles of DOM. This study identified a specific mechanism by which biochar affects Hg behavior in rice paddy soil and contributes to understanding the more general influence of biochar in agriculture and contaminant remediation. [Display omitted]