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(14)C-磺胺嘧啶和(14)C-二氟沙星在粪肥储存过程中的行为。

Behaviour of (14)C-sulfadiazine and (14)C-difloxacin during manure storage.

机构信息

Institute of Environmental Research (INFU), TU Dortmund, Dortmund, Germany.

出版信息

Sci Total Environ. 2010 Mar 1;408(7):1563-8. doi: 10.1016/j.scitotenv.2009.12.010. Epub 2009 Dec 21.

DOI:10.1016/j.scitotenv.2009.12.010
PMID:20022355
Abstract

The persistence of sulfadiazine, difloxacin, and their metabolites has been investigated in stored manure. The manure collected from sulfadiazine ((14)C-SDZ) and difloxacin ((14)C-DIF) treated pigs contained N-acetylsulfadiazine (Ac-SDZ), 4-hydroxy-SDZ (4-OH-SDZ), and sarafloxacin (SARA) as the main metabolites, respectively along with their parent compounds. Manures were stored separately at 10 degrees C and 20 degrees C at various moisture levels. About 96-99% of the radioactivity remained in extractable parent compounds and their metabolites after 150d of storage. The formation of non-extractable residue and the rate of mineralization were both negligible in manure containing SDZ and DIF. During storage SDZ concentration increased as a result of the deacetylation of Ac-SDZ, whose concentration decreased proportionally. Hence the environmental effects may be underestimated if the parent compound alone is considered for environmental risk assessment. About 11% and 14% of 4-OH-SDZ were lost after 20 and 40d of storage; thereafter its concentration increased relatively, highlighting hydroxylation of SDZ. DIF degraded very slowly (7% loss after 150d) during the storage of manure; in contrast the concentration of SARA decreased rapidly (72-90% loss after 150d). Dilution of manure and storage at higher temperatures for a reasonable period of time enhanced the rate of reactions of SDZ, DIF and their related metabolites.

摘要

磺胺嘧啶和二氟沙星及其代谢物在储存的粪便中的持久性已被研究过。从磺胺嘧啶((14)C-SDZ)和二氟沙星((14)C-DIF)处理的猪收集的粪便中,分别含有 N-乙酰磺胺嘧啶(Ac-SDZ)、4-羟基磺胺嘧啶(4-OH-SDZ)和沙拉氟沙星(SARA)作为主要代谢物,以及它们的母体化合物。粪便分别在 10 度和 20 度下储存在不同的水分水平下。在储存 150 天后,大约 96-99%的放射性物质仍存在于可提取的母体化合物及其代谢物中。在含有 SDZ 和 DIF 的粪便中,非可提取残留的形成和矿化速率都可以忽略不计。在储存过程中,由于 Ac-SDZ 的脱乙酰化作用,SDZ 的浓度增加,而 Ac-SDZ 的浓度则相应降低。因此,如果仅考虑母体化合物进行环境风险评估,可能会低估环境影响。在储存 20 和 40 天后,4-OH-SDZ 分别损失了约 11%和 14%;此后,其浓度相对增加,突出了 SDZ 的羟化作用。在粪便储存期间,DIF 非常缓慢降解(150 天后损失 7%);相比之下,SARA 的浓度迅速下降(150 天后损失 72-90%)。粪便的稀释和在较高温度下储存一段时间可以提高 SDZ、DIF 及其相关代谢物的反应速率。

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