首页> 外文期刊>Journal of Environmental Science and Health. Part B, Pesticides, Food Contaminants and Agricultural Wastes >Speciation and persistence of doxycycline in the aquatic environment: Characterization in terms of steady state kinetics
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Speciation and persistence of doxycycline in the aquatic environment: Characterization in terms of steady state kinetics

机译:强力霉素在水生环境中的形态和持久性:稳态动力学表征

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The aim of the present work was to establish the kinetics for the degradation of doxycycline in the aquatic environment with a view to arriving at a kinetic model that can be used to predict the persistence of antibiotic with confidence. The degradation of doxycycline in both water and sediment phases of aquatic microcosm experiments, as well as in distilled water control experiments, was studied over a period of 90 days. An initial 21% loss due to adsorption by the sediment was observed in the microcosm experiment soon after charging. Biphasic zero-order linear rates of degradation, attributed to microbial degradation of the free and sediment or colloidal particle-adsorbed antibiotic, were observed for both water phase (2.3 × 10~(-2) and 4.5 × 10~(-3) μgg(-1) day(-1)) and sediment phase (7.9 × 10~(-3) and 1.5 × 10~(-3) μgg(-1) day(-1)) of the microcosm experiment. The covered distilled water control experiment exhibited a monophasic zero-order linear rate (1.9 × 10~(-3) μgg(-1) day(-1)) attributed to hydrolysis, while the distilled water experiment exposed to natural light exhibited biphasic liner rates attributed to a combination of hydrolysis and photolysis (2.9 × 10~(-3) μgg(-1) day~(-1) ) and to microbial degradation (9.8 × 10~(-3) μgg(-1) day(-1)). A kinetic model that takes into account hydrolysis, photolysis, microbial degradation as well as sorption/desorption by colloidal and sediment particles is presented to account for the observed zero-order kinetics. The implications of the observed kinetics on the persistence of doxycycline in the aquatic environment are discussed.
机译:本工作的目的是建立在水生环境中强力霉素降解的动力学,以期建立一个可用于预测抗生素持久性的动力学模型。在90天的时间内研究了水力微观实验以及蒸馏水控制实验中水和沉积相中强力霉素的降解。装料后不久,在微观实验中观察到由于沉积物吸附引起的最初21%的损失。在水相(2.3×10〜(-2)和4.5×10〜(-3)μgg的水相中均观察到归因于游离和沉积物或胶体颗粒吸附抗生素的微生物降解的双相零级线性降解速率(-1)天(-1))和沉积物相(7.9×10〜(-3)和1.5×10〜(-3)μgg(-1)天(-1))。覆盖的蒸馏水控制实验表现出归因于水解的单相零级线性速率(1.9×10〜(-3)μgg(-1)day(-1)),而暴露于自然光下的蒸馏水实验则表现出双相线性归因于水解和光解的组合(2.9×10〜(-3)μgg(-1)天〜(-1))和微生物降解(9.8×10〜(-3)μgg(-1)天( -1))。提出了考虑了水解,光解,微生物降解以及胶体和沉积物颗粒的吸附/解吸的动力学模型,以说明观察到的零级动力学。讨论了观察到的动力学对强力霉素在水生环境中持久性的影响。

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