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四种头孢菌素抗生素在湖泊地表水和沉积物中的生物和非生物降解。

Biotic and abiotic degradation of four cephalosporin antibiotics in a lake surface water and sediment.

机构信息

State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing 210093, China.

出版信息

Chemosphere. 2010 Sep;80(11):1399-405. doi: 10.1016/j.chemosphere.2010.05.048. Epub 2010 Jun 25.

Abstract

Cephalosporins are widely used veterinary and human antibiotics, but their environmental fate and impacts are still unclear. We studied degradation of four cephalosporins (cefradine, cefuroxime, ceftriaxone, and cefepime) from each generation in the surface water and sediment of Lake Xuanwu, China. The four cephalosporins degraded abiotically in the surface water in the dark with half-lives of 2.7-18.7d, which were almost the same as that in sterilized surface water. Under exposure to simulated sunlight, the half-lives of the cephalosporins decreased significantly to 2.2-5.0d, with the maximal decrease for ceftriaxone from 18.7d in the dark to 4.1d under the light exposure. Effects of dissolved organic matter (DOM) and nitrate on photodegradation of the cephalosporins were compound-specific. While DOM (5 mg L(-1)) stimulated the photodegradation of only cefradine (by 9%) and cefepime (by 34%), nitrate (10 microM) had effects only on cefepime (stimulation by 13%). Elimination rates of the cephalosporins in oxic sediment (half-lives of 0.8-3.1d) were higher than in anoxic sediment (half-lives of 1.1-4.1d), mainly attributed to biodegradation. The data indicate that abiotic hydrolysis (for cefradine, cefuroxime, and cefepime) and direct photolysis (for ceftriaxone) were the primary processes for elimination of the cephalosporins in the surface water of the lake, whereas biodegradation was responsible for the elimination of the cephalosporins in the sediment. Further studies are needed on chemical structure, toxicity, and persistence of transformation products of the cephalosporins in the environment.

摘要

头孢菌素类广泛用于兽医和人类抗生素,但它们的环境命运和影响仍不清楚。我们研究了来自中国玄武湖地表水和底泥中的四代头孢菌素(头孢拉定、头孢呋辛、头孢曲松和头孢吡肟)的降解情况。在黑暗中,这四种头孢菌素在地表水中无生物降解,半衰期为 2.7-18.7d,几乎与灭菌地表水中的半衰期相同。在模拟阳光照射下,头孢菌素的半衰期显著缩短至 2.2-5.0d,其中头孢曲松的半衰期从黑暗中的 18.7d 缩短至光照下的 4.1d。溶解有机物(DOM)和硝酸盐对头孢菌素光降解的影响具有特异性。虽然 DOM(5mg/L)仅刺激头孢拉定(增加 9%)和头孢吡肟(增加 34%)的光降解,但硝酸盐(10μM)仅对头孢吡肟有影响(增加 13%)。在好氧沉积物中(半衰期为 0.8-3.1d),头孢菌素的消除率高于缺氧沉积物(半衰期为 1.1-4.1d),主要归因于生物降解。数据表明,在湖泊表面水中,头孢菌素的主要消除过程是无差水解(对于头孢拉定、头孢呋辛和头孢吡肟)和直接光解(对于头孢曲松),而生物降解是头孢菌素在沉积物中消除的主要原因。需要进一步研究头孢菌素在环境中的化学结构、毒性和转化产物的持久性。

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