Jiang Liu, Lei Zhao, Kun Kong, Mahmoud A Abdelhafiz, Shanyi Tian, Tao Jiang, Bo Meng, Xinbin Feng
Journal: Journal of hazardous materials 2022;433():128752
PMID: 35364530
The newly deposited mercury (Hg) is more readily methylated to methylmercury (MeHg) than native Hg in paddy soil. However, the biogeochemical processes of the newly deposited Hg in soil are still unknown. Here, a field experimental plot together with a stable Hg isotope tracing technique was used to demonstrate the geochemical fractionation (partitioning and redistribution) of the newly deposited Hg in paddy soils during the rice-growing period. We showed that the majority of Hg tracer (Hg, 115.09 ± 0.36 μg kg) was partitioned as organic matter bound Hg (84.6-89.4%), followed by residual Hg (7.6-8.1%), Fe/Mn oxides bound Hg (2.8-7.2%), soluble and exchangeable Hg (0.05-0.2%), and carbonates bound Hg (0.04-0.07%) in paddy soils. Correlation analysis and partial least squares path modeling revealed that the coupling of autochthonous dissolved organic matter and poorly crystalline Fe (oxyhydr)oxides played a predominant role in controlling the redistribution of the newly deposited Hg among geochemical fractions (i.e., fraction changes). The expected aging processes of the newly deposited Hg were absent, potentially explaining the high bioavailability of these Hg in paddy soil. This study implies that other Hg pools (e.g., organic matter bound Hg) should be considered instead of merely soluble Hg pools when evaluating the environmental risks of Hg from atmospheric depositions.
Copyright © 2022 Elsevier B.V. All rights reserved.
Medical:
Full Text Sources:
© Copyright 2026, Nutrition Evidence
We use cookies to improve your experience and analyze site traffic with Google Analytics. By continuing to use our site, you agree to our use of cookies. Learn more.