Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences , Nanjing 210008, People's Republic of China.
Environ Sci Technol. 2014;48(3):1902-10. doi: 10.1021/es4048126. Epub 2014 Jan 21.
We investigated the activation of hydrogen peroxide (H2O2) by biochars (produced from pine needles, wheat, and maize straw) for 2-chlorobiphenyl (2-CB) degradation in the present study. It was found that H2O2 can be effectively activated by biochar, which produces hydroxyl radical ((•)OH) to degrade 2-CB. Furthermore, the activation mechanism was elucidated by electron paramagnetic resonance (EPR) and salicylic acid (SA) trapping techniques. The results showed that biochar contains persistent free radicals (PFRs), typically ∼ 10(18) unpaired spins/gram. Higher trapped [(•)OH] concentrations were observed with larger decreases in PFRs concentration, when H2O2 was added to biochar, indicating that PFRs were the main contributor to the formation of (•)OH. This hypothesis was supported by the linear correlations between PFRs concentration and trapped [(•)OH], as well as kobs of 2-CB degradation. The correlation coefficients (R(2)) were 0.723 and 0.668 for PFRs concentration vs trapped [(•)OH], and PFRs concentration vs kobs, respectively, when all biochars pyrolyzed at different temperatures were included. For the same biochar washed by different organic solvents (methanol, hexane, dichloromethane, and toluene), the correlation coefficients markedly increased to 0.818-0.907. Single-electron transfer from PFRs to H2O2 was a possible mechanism for H2O2 activation by biochars, which was supported by free radical quenching studies. The findings of this study provide a new pathway for biochar implication and insight into the mechanism of H2O2 activation by carbonaceous materials (e.g., activated carbon and graphite).
本研究考察了生物炭(由松针、小麦和玉米秸秆制成)对 2-氯联苯(2-CB)降解中过氧化氢(H2O2)的活化作用。结果发现,生物炭可以有效地活化 H2O2,产生羟基自由基((•)OH)来降解 2-CB。此外,通过电子顺磁共振(EPR)和水杨酸(SA)捕获技术阐明了其活化机制。结果表明,生物炭中含有持久自由基(PFRs),通常约为 10(18)个未配对的自旋/克。当 H2O2 加入到生物炭中时,PFRs 浓度的降低与[(•)OH]捕获浓度的增加成正比,表明 PFRs 是形成(•)OH 的主要原因。这一假设得到了 PFRs 浓度与捕获的[(•)OH]以及 2-CB 降解的表观速率常数(kobs)之间线性关系的支持。当包括所有在不同温度下热解的生物炭时,PFRs 浓度与[(•)OH]之间以及 PFRs 浓度与 kobs 之间的相关系数(R(2))分别为 0.723 和 0.668。对于用不同有机溶剂(甲醇、己烷、二氯甲烷和甲苯)洗涤的相同生物炭,相关系数显著增加到 0.818-0.907。从 PFRs 到 H2O2 的单电子转移可能是生物炭活化 H2O2 的一种机制,自由基猝灭研究支持这一机制。本研究的结果为生物炭的应用提供了新途径,并深入了解了碳质材料(如活性炭和石墨)活化 H2O2 的机制。