期刊文献+

络合剂强化KMnO_4氧化降解酚类化合物的研究 被引量:4

Ligand-enhanced Oxidation of Phenolic Compounds by Permanganate
原文传递
导出
摘要 研究了磷酸盐、焦磷酸、EDTA等络合剂对KMnO。氧化降解酚类化合物(苯酚、2-氯酚、4-氯酚和2,4-二氯酚)的强化作用。结果表明,在磷酸根浓度为0~50mmol/L、pH值为4.0~9.0的条件下,强化作用随磷酸根浓度的增大或pH的降低而逐渐增强。络合剂通过络合配位作用使得KMnO4氧化降解酚类化合物过程中原位生成的中间价态锰的存活时间延长、稳定性增强,使其氧化能力得到有效利用,从而提高了KMnO4氧化降解酚类化合物的效果;相反,无络合剂存在时,原位生成的中间价态锰会迅速自分解或歧化生成最终稳定态MnO2,其氧化能力难以得到发挥。天然大分子有机物腐殖酸和天然水体由于其络合配位作用,也具有强化KMnO2氧化降解酚类化合物的能力。 The enhancement effects of ligands such as phosphate, pyrophosphate and EDTA on permanganate oxidation of phenolic compounds (phenol, 2-chlorophenol, 4-chlorophenol, and 2,4-dichlorophenol) were investigated. Under the conditions of phosphate 0 to 50 mmol/L and pH 4.0 to 9.0, the enhancement effect is enhanced with the increase of the phosphate concentration or the decrease of pH. In situ formed manganese intermediates during oxidation of phenolic compounds by permanganate can have longer survival time, be excellently stabilized and maximize the oxidation capacity in the pres- ence of ligands, and thus the oxidation effect of phenolic compounds is improved, whereas in the absence of ligands, the in situ formed manganese intermediates can be self-decomposed or be disproportionated to yield stable MnO2, and the oxidation capacity is difficultly fulfilled. Macromolecular humic acid and natural waters, due to their ability to complex metal ions, are also capable of enhancing permanganate oxidation of phenolic compounds.
出处 《中国给水排水》 CAS CSCD 北大核心 2010年第17期85-88,共4页 China Water & Wastewater
基金 国家科技支撑计划项目(2006BAJ08B05) 国家水体污染控制与治理科技重大专项(2009ZX07424-005 2009ZX07424-006)
关键词 络合剂 KMNO4 酚类化合物 ligands potassium permanganate phenolie compounds
  • 相关文献

参考文献13

  • 1刘可,马军,关小红,秦庆东,余敏.新生态铁锰氧化物混凝除磷效果研究[J].中国给水排水,2009,25(21):89-90. 被引量:9
  • 2李伟光,郜玉楠,黄晓东,孙士权,张金松.高锰酸钾与粉末活性炭联用去除饮用水中嗅味[J].中国给水排水,2007,23(5):18-21. 被引量:24
  • 3Walker H W,Bob M M.Stability of particle flocs upon addition of natural organic matter under quiescent conditions[J].Water Res,2001,35(4):875-882.
  • 4Waldemer R H,Tratnyek P G.Kinetics of contaminant degradation by permanganate[J].Environ Sci Technol,2006,40(3):1055-1061.
  • 5Kim K,Gurol M D.Reaction of nonaqueous phase TCE with permanganate[J].Environ Sci Technol,2005,39(23):9303-9308.
  • 6Lee E S,Seol Y,Fang Y C,et al.Destruction efficiencies and dynamics of reaction fronts associated with the permanganate oxidation of trichloroethylene[J].Environ Sci Technol,2003,37(11):2540-2546.
  • 7Chang H S,Korshin G V,Ferguson J F.Investigation of mechanisms of oxidation of EDTA and NTA by permanganate at high pH[J].Environ Sci Technol,2006,40(16):5089-5094.
  • 8Thabaj K A,Kulkarni S D,Chimatadar S A,et al.Oxidative transformation of ciprofloxacin by alkaline permanganate-A kinetic and mechanistic study[J].Polyhedron,2007,26(17):4877-4885.
  • 9Ma J,Jiang J,Pang S Y,et al.Adsorptive fractionation of humic acid at air-water interfaces[J].Environ Sci Technol,2007,41(14):4959-4964.
  • 10Hu L H,Martin H M,Arce-Bulted O,et al.Oxidation of carbamazepine by Mn(Ⅶ)and Fe(Ⅵ):reaction kinetics and mechanism[J].Environ Sci Technol,2009,43(2):509-515.

二级参考文献9

共引文献31

同被引文献40

引证文献4

二级引证文献6

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部