State Key Laboratory of Pollution Control and Resources Reuse, Tongji University , Shanghai 20092, People's Republic of China.
State Key Laboratory of Urban Water Resource and Environment, Harbin Institute of Technology , Harbin 150090, People's Republic of China.
Environ Sci Technol. 2015 Oct 20;49(20):12414-21. doi: 10.1021/acs.est.5b03111. Epub 2015 Oct 9.
MnO4(-) was activated by HSO3(-), resulting in a process that oxidizes organic contaminants at extraordinarily high rates. The permanganate/bisulfite (PM/BS) process oxidized phenol, ciprofloxacin, and methyl blue at pHini 5.0 with rates (kobs ≈ 60-150 s(-1)) that were 5-6 orders of magnitude faster than those measured for permanganate alone, and ∼5 to 7 orders of magnitude faster than conventional advanced oxidation processes for water treatment. Oxidation of phenol was fastest at pH 4.0, but still effective at pH 7.0, and only slightly slower when performed in tap water. A smaller, but still considerable (∼3 orders of magnitude) increase in oxidation rates of methyl blue was observed with MnO2 activated by HSO3(-) (MO/BS). The above results, time-resolved spectroscopy of manganese species under various conditions, stoichiometric analysis of pH changes, and the effect of pyrophosphate on UV absorbance spectra suggest that the reactive intermediate(s) responsible for the extremely rapid oxidation of organic contaminants in the PM/BS process involve manganese(III) species with minimal stabilization by complexation. The PM/BS process may lead to a new category of advanced oxidation technologies based on contaminant oxidation by reactive manganese(III) species, rather than hydroxyl and sulfate radicals.
过二硫酸盐活化高锰酸盐,以极高的速率氧化有机污染物。在初始 pH 值为 5.0 的条件下,高锰酸盐/亚硫酸盐(PM/BS)工艺可氧化苯酚、环丙沙星和亚甲基蓝,其速率(kobs≈60-150 s-1)比单独使用高锰酸盐的测量值快 5-6 个数量级,比传统的水处理高级氧化工艺快 5-7 个数量级。在 pH 4.0 时,苯酚的氧化速度最快,但在 pH 7.0 时仍然有效,在自来水中进行时仅略慢。用 HSO3- 活化的 MnO2(MO/BS)观察到亚甲基蓝的氧化速率略有增加(约 3 个数量级)。上述结果、各种条件下锰物种的时间分辨光谱、pH 值变化的化学计量分析以及焦磷酸盐对紫外吸收光谱的影响表明,在 PM/BS 工艺中,导致有机污染物快速氧化的反应性中间体涉及锰(III)物种,其通过络合最小程度稳定。PM/BS 工艺可能会导致一种新型的高级氧化技术,该技术基于反应性锰(III)物种对污染物的氧化作用,而不是羟基自由基和硫酸根自由基。