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鉴定臭氧和高级氧化工艺处理产生的红霉素 A 降解产物。

Identification of degradation products of erythromycin A arising from ozone and advanced oxidation process treatment.

机构信息

LEMA-Laboratory of Energy and Environment, Chemical and Food Engineering Department, Technology Center, Federal University of Santa Catarina, Florianópolis, Brazil.

出版信息

Water Environ Res. 2010 Sep-Oct;82(9):797-805. doi: 10.2175/106143010x12609736966928.

Abstract

The degradation products of the macrolide antibiotic erythromycin A (ERY) arising from direct ozone attack and hydroxyl radical attack are presented for the first time. Ozone treatment was carried out by spiking ozone stock solutions to solutions containing ERY-ERY:O3 = 1:5 and 1:10 (M:M), while, in parallel, t-BuOH was used as a hydroxyl radical (*OH) scavenger. The advanced oxidation processes (AOPs) O3/UV, O3/H2O2, and UV/H2O2 were carried out to recognize and verify possible differences between their primary degradation products; the initial concentrations were ERY:O3 = 1:5 (M:M), ERY:O3:H202 = 1:5:5 (M:M:M), or ERY:H202 = 1:5 (M:M), respectively. Six degradation products were identified from ozonation-one originates from direct ozone attack on the tertiary amine group, while the others arise from radical ion attack, which might be formed during degradation of O3 in water. Fewer primary degradation products were observed arising from *OH-based treatments (AOP) than from ozonation, possibly because the reaction of *OH radicals is non-selective and typically is diffusion-controlled. Four degradation products were detected by *OH radical attacks; two of them already were observed during ozonation, with one as an oxidized ERY molecule and the other as a non-oxidized fragment of the ERY molecule.

摘要

本文首次提出了直接臭氧攻击和羟基自由基攻击导致的大环内酯类抗生素红霉素 A(ERY)的降解产物。通过向含有 ERY-ERY:O3 = 1:5 和 1:10(M:M)的溶液中投加臭氧储备溶液进行臭氧处理,同时,使用 t-BuOH 作为羟基自由基(*OH)清除剂。进行了高级氧化工艺(AOPs)O3/UV、O3/H2O2 和 UV/H2O2,以识别和验证它们的主要降解产物之间可能存在的差异;初始浓度分别为 ERY:O3 = 1:5(M:M)、ERY:O3:H202 = 1:5:5(M:M:M)或 ERY:H202 = 1:5(M:M)。从臭氧化中鉴定出了 6 种降解产物-一种源自叔胺基团的直接臭氧攻击,而其他产物则源自自由基离子攻击,这可能是在水中降解臭氧时形成的。与臭氧化相比,基于 *OH 的处理(AOP)观察到的主要降解产物较少,这可能是因为 *OH 自由基的反应是非选择性的,并且通常受扩散控制。通过 *OH 自由基攻击检测到 4 种降解产物;其中两种在臭氧化过程中已经观察到,一种是氧化的 ERY 分子,另一种是非氧化的 ERY 分子片段。

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