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土霉素与水合氧化锰反应的动力学

Kinetics of oxytetracycline reaction with a hydrous manganese oxide.

作者信息

Rubert Kennedy F, Pedersen Joel A

机构信息

Molecular and Environmental Toxicology Center, University of Wisconsin, Madison, Wisconsin 53706, USA.

出版信息

Environ Sci Technol. 2006 Dec 1;40(23):7216-21. doi: 10.1021/es060357o.

Abstract

Tetracycline antibiotics comprise a class of broad spectrum antimicrobial agents finding application in human therapy, animal husbandry, aquaculture, and fruit crop production. To better understand the processes affecting these antibiotics in soils and sediments, the kinetics of oxytetracycline transformation by a hydrous manganese oxide (MnO2) were investigated as a function of reactant concentration, pH, and temperature. Oxytetracycline was rapidly degraded by MnO2. Initial reaction rates exhibited pronounced pH-dependence, increasing as pH decreased. Reaction of oxytetracycline with MnO2 was accompanied by generation of Mn(II) ions, suggesting oxidative transformation of the antibiotic. At pH 5.6, apparent reaction orders for oxytetracycline and MnO2 were 0.7 and 0.8. Reaction order with respect to H+ was 0.6 between pH 4 and 9. Initial reaction rates increased by a factor of approximately 2.4 for 10 degrees C temperature increases; the apparent activation energy (60 kJ x mol(-1)) was consistent with a surface-controlled reaction. Reactivity of tetracycline antibiotics toward MnO2 increased in the following order: rolitetracyline oxytetracycline < or =tetracycline approximately meclocycline < chlortetracycline. The initial rate of chlortetracycline degradation by MnO2 was substantially larger than that of the other tetracycline antibiotics investigated. MnO2 reactivity toward oxytetracycline decreased with time; a retarded rate equation was used to describe oxytetracycline reaction with MnO2 under declining rate conditions. This study indicates that natural manganese oxides in soils and sediments are likely to promote appreciable degradation of tetracycline antibiotics, and that reaction rates are strongly dependent on reaction time scale and solution conditions.

摘要

四环素类抗生素是一类广谱抗菌剂,在人类治疗、畜牧业、水产养殖和水果作物生产中都有应用。为了更好地了解土壤和沉积物中影响这些抗生素的过程,研究了水合氧化锰(MnO₂)对土霉素转化的动力学,该动力学是反应物浓度、pH值和温度的函数。土霉素被MnO₂迅速降解。初始反应速率表现出明显的pH依赖性,随着pH值降低而增加。土霉素与MnO₂的反应伴随着Mn(II)离子的生成,这表明抗生素发生了氧化转化。在pH 5.6时,土霉素和MnO₂的表观反应级数分别为0.7和0.8。在pH 4至9之间,相对于H⁺的反应级数为0.6。温度每升高10℃,初始反应速率增加约2.4倍;表观活化能(60 kJ·mol⁻¹)与表面控制反应一致。四环素类抗生素对MnO₂的反应活性按以下顺序增加:罗利环素<土霉素≤四环素≈美他环素<金霉素。MnO₂降解金霉素的初始速率明显大于所研究的其他四环素类抗生素。MnO₂对土霉素的反应活性随时间降低;采用减速速率方程来描述土霉素在速率下降条件下与MnO₂的反应。本研究表明,土壤和沉积物中的天然锰氧化物可能会促进四环素类抗生素的显著降解,且反应速率强烈依赖于反应时间尺度和溶液条件。

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