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Biological and chemical degradation of azo dyes under aerobic conditions.

机译:有氧条件下偶氮染料的生物和化学降解。

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摘要

Azo dyes represent {dollar}>{dollar}50% of synthetic industrial dyes. Azo dyes are recalcitrant to aerobic bacterial degradation. Reductive cleavage of the azo linkage under anaerobic conditions yields potentially carcinogenic aromatic amines. This thesis examines aerobic azo dye degradation by the white-rot fungus Phanerochaete chrysosporium, by peroxidases, and by hydroxyl radicals.; P. chrysosporium, a lignin-degrading basidiomycete, extensively mineralized several hydrophobic azo dyes over a 12-day period. All dyes were degraded most extensively in ligninolytic cultures. Hydroxyl, acetamido, nitro, and N-alkylamino substituents enhanced dye degradation.; Disperse Yellow 3 (DY3, 2-(4{dollar}spprime{dollar}-acetamidophenylazo) -4-methylphenol), a dye mineralized by P. chrysosporium, yielded acetanilide as a major metabolite during fungal degradation in cultures that produce lignin and manganese peroxidases (LiP and MnP). Degradation of DY3 by LiP, Mn(III)-malonate (a MnP mimic), and horseradish peroxidase (HRP) was studied. The major products were acetanilide, 4-methyl-1,2-benzoquinone, and dimerized DY3. A mechanism for DY3 degradation is suggested. Either Mn(III) or the H{dollar}sb2{dollar}O{dollar}sb2{dollar}-oxidized forms of the peroxidases oxidize the phenolic ring of the dye by two electrons, producing an azo-bearing carbonium ion. Hydrolytic azo cleavage forms the quinone product and an acetamidophenyldiazene intermediate. The acetamidophenyldiazene is oxidized by metal or oxygen to produce an acetamidophenyldiazenyl radical, which cleaves homolytically to acetamidophenyl radical and molecular nitrogen. The acetamidophenyl radical abstracts a hydrogen from the surroundings, yielding acetanilide. Consistent with this mechanism, dyes containing phenylazo substitutions were degraded to quinones and benzenes by HRP. Further support for the mechanism was obtained through deuterium labeling studies.; Hydroxyl radicals, produced for 24 h by reaction of ferric nitrate and hydrogen peroxide at pH 2.8, degraded large amounts of hydrophobic azo dyes to CO{dollar}sp2{dollar} and water-soluble compounds. Products included benzene, formed during degradation of phenylazo-substituted dyes, and aliphatic acids. A mechanism resembling that for the peroxidase-catalyzed degradation of azo dyes is proposed for dye degradation by hydroxyl radical.
机译:偶氮染料占合成工业染料的50%。偶氮染料对需氧细菌降解具有顽固性。在厌氧条件下偶氮键的还原裂解会产生潜在的致癌芳香胺。本文研究了白腐真菌Phanerochaete chrysosporium,过氧化物酶和羟基自由基对好氧偶氮染料的降解。木质素降解的担子菌P. chrysosporium在12天的时间内广泛矿化了几种疏水性偶氮染料。在木质素分解培养物中,所有染料均被最广泛地降解。羟基,乙酰氨基,硝基和N-烷基氨基取代基增强了染料的降解。分散黄3(DY3,2-(4 {dol}} spprime {dollar}-乙酰氨基苯基偶氮)-4-甲基苯酚),一种由金孢霉(P. chrysosporium)矿化的染料,在产生木质素和锰的培养物的真菌降解过程中,乙酰苯胺是主要的代谢产物。过氧化物酶(LiP和MnP)。研究了LiP,Mn(III)-丙二酸(模拟MnP)和辣根过氧化物酶(HRP)对DY3的降解。主要产物是乙酰苯胺,4-甲基-1,2-苯醌和二聚化的DY3。建议了DY3降解的机制。 Mn(III)或过氧化物的H {sb2} {O} {sb2 {sol2}}氧化形式均可通过两个电子将染料的酚环氧化,从而产生一个含偶氮的碳离子。水解偶氮裂解形成醌产物和乙酰氨基苯基二氮杂中间体。乙酰氨基苯基二氮烯被金属或氧气氧化,生成乙酰氨基苯基二氮烯基,该自由基均裂为乙酰氨基苯基基团和分子氮。乙酰胺基苯基从周围提取氢,生成乙酰苯胺。与此机理一致,含有苯偶氮取代基的染料被HRP降解为醌和苯。通过氘标记研究获得了对该机制的进一步支持。通过硝酸铁和过氧化氢在pH 2.8的反应产生24小时的羟基自由基,将大量的疏水偶氮染料降解为CO {dol} sp2 {dollar}和水溶性化合物。产物包括苯(在偶氮苯基取代的染料降解过程中形成)和脂肪酸。对于过氧化物酶催化的偶氮染料的降解,提出了类似于通过羟基自由基降解染料的机理。

著录项

  • 作者

    Spadaro, Jack Thomas.;

  • 作者单位

    Oregon Graduate Institute of Science and Technology.;

  • 授予单位 Oregon Graduate Institute of Science and Technology.;
  • 学科 Environmental Sciences.; Biology Microbiology.
  • 学位 Ph.D.
  • 年度 1994
  • 页码 138 p.
  • 总页数 138
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 环境科学基础理论;微生物学;
  • 关键词

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