School of Urban and Environmental Sciences, Key Laboratory of the Ministry of Education for Earth Surface Processes, Peking University, Beijing 100871, China.
State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Jiangsu 210046, China.
Environ Sci Technol. 2020 Sep 15;54(18):11137-11145. doi: 10.1021/acs.est.0c01132. Epub 2020 Aug 31.
Here, we investigated the photoreduction of Hg(II) (Hg(NO)) mediated by dissolved black carbon (DBC, <0.45 μm size fraction) collected from water extracts of biochar derived by pyrolyzing crop residues (rice, soybean, and peanut). Under simulated sunlight conditions, the presence of 5 mg C/L DBC significantly facilitated the production of Hg(0) from Hg(II) (initially at 10 nmol/L) with a reduction ratio of 73 ± 4% in 5.3 h. Inhibition of photolysis-induced reactive oxygen species by a quencher or removal of dissolved oxygen indicated that Hg(II) was mainly reduced by superoxide anion (O). Reduction by electrons transferred from photoexcited DBC components or by organic free radicals produced from photo-Fenton-like reactions was also proposed to play a role. Contrary to dissolved humic substances, the DBC-mediated photoreduction of Hg(II) led to unique positive mass-independent isotopic fractionation (MIF) of Hg(0) (ΔHg = 1.8 ± 0.3‰), which was attributed to the dominance of secondary Hg(II) reduction by O. The leachate from soil amended with rice biochar at 1-5% mass ratios exhibited significantly higher photocatalytic efficiency than that from unamended soil (wherein the reduced Hg(0) increased from 27 ± 1 to 63 ± 2% in maximum), and the efficiency positively correlated with the percentage of amended biochar. Under natural illumination conditions, the total mercury and/or methylmercury uptake by roots, shoots, and leaves of lettuce ( L.) grown in water extracts of rice biochar-amended soil was consistently lower (up to 70 ± 20%) than that without the biochar amendment. The findings highlight that DBC might play an important and previously unrecognized role in the biogeochemical cycle and the environmental impact of mercury.
在这里,我们研究了由来源于热解农作物残渣(水稻、大豆和花生)生物炭的水提取物中收集的溶解态黑碳(<0.45μm 粒径)介导的 Hg(II)(Hg(NO))的光还原作用。在模拟太阳光条件下,5mg C/L DBC 的存在显著促进了 Hg(II)(初始浓度为 10nmol/L)向 Hg(0)的生成,在 5.3 小时内还原率达到 73±4%。通过猝灭剂抑制光解诱导的活性氧或去除溶解氧表明,Hg(II)主要通过超氧阴离子(O)还原。从光激发的 DBC 成分转移的电子或光芬顿样反应产生的有机自由基的还原也被认为起到了一定作用。与溶解态腐殖质不同,DBC 介导的 Hg(II)光还原导致 Hg(0)的独特的正质量独立同位素分馏(MIF)(ΔHg=1.8±0.3‰),这归因于 O 主导的二次 Hg(II)还原。以 1-5%质量比添加水稻生物炭的土壤浸出液表现出明显高于未添加土壤的光催化效率(其中最大还原 Hg(0)从 27±1%增加到 63±2%),并且效率与添加生物炭的百分比呈正相关。在自然光照射条件下,生长在添加水稻生物炭的土壤水提取物中的生菜( L.)的根、茎和叶对总汞和/或甲基汞的吸收始终低于未添加生物炭的吸收(低至 70±20%)。这些发现强调了 DBC 可能在汞的生物地球化学循环和环境影响中发挥重要的、以前未被认识到的作用。