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Sunlight-induced degradation of soil-adsorbed veterinary antimicrobials Marbofloxacin and Enrofloxacin

机译:阳光诱导的土壤吸附的兽用抗菌药物马立沙星和恩诺沙星的降解

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Marbofloxacin (MAR) and Enrofloxacin (ENR), two largely employed veterinary Fluoroquinolones (FQs), were found to be present at the micrograms per kilogram level in agricultural soils of South Lombardy (Italy) several months after manuring. Distribution coefficients (K_d) from sorption experiments indicated a strong binding to the soil. Soil samples fortified with environmentally significant FQs amounts (0.5 mg kg~(-1) were exposed to solar light that promoted extensive degradation (80%) of both drugs in 60-150 h. Thus, photochemistry could be considered a significant depollution path in the soil, although it was two orders of magnitudes slower than in aqueous solution and a fraction of the drug (ca. 20%) remained unaffected. For MAR the photoprocess was the same as in solution, and involved cleavage of the tetrahydrooxadiazine ring. On the contrary, with ENR only some of the photoproducts determined in water (those arising from a stepwise oxidation of the piperazine side chain) were observed. Substitution of the 6-fluoro by a hydroxyl group and reduction did not occur in the soil, supporting the previous contention that such processes required polar solvation of FQs. Consistently with this rationalization, the irradiation of thin layers of solid drugs led to essentially the same products distribution as in the soil. From the environmental point of view it is important to notice that photodegradation mainly affects the side-chains, while the fluoroquinolone ring, to which the biological effect is associated, is conserved up to the later stages of the degradation.
机译:饲喂几个月后,在意大利南部伦巴第的农业土壤中发现了两种主要使用的兽用氟喹诺酮类药物(Marofloxacin,MAR)和恩诺沙星(Enrofloxacin,ENR),每千克的微克水平为毫克。吸附实验的分布系数(K_d)表明与土壤有很强的结合力。在环境中添加了FQs量极高(0.5 mg kg〜(-1))的土壤样品,在60-150 h内暴露于太阳光下,可促进两种药物的广泛降解(80%),因此,光化学可被认为是土壤中重要的污染途径。在土壤中,尽管它比在水溶液中慢两个数量级,并且一部分药物(约20%)没有受到影响;对于MAR,光过程与在溶液中相同,并涉及四氢恶二嗪环的裂解。相反,在ENR中,仅观察到一些在水中测定的光产物(由哌嗪侧链的逐步氧化产生的光产物),在土壤中未发生6-氟被羟基取代和还原的现象,这支持了先前的论点是,此类过程需要极性溶剂化物(FQ)的极性化,与此合理化一致的是,对固体药物薄层的照射导致与土壤中基本相同的产品分布。从环境的角度来看,重要的是要注意光降解主要影响侧链,而与生物学效应相关的氟喹诺酮环则一直保留到降解的后期。

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