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从土壤特性估算土霉素和金霉素的吸附/解吸 Freundlich 亲合系数:实验数据和土壤转移函数。

Estimation of adsorption/desorption Freundlich's affinity coefficients for oxytetracycline and chlortetracycline from soil properties: Experimental data and pedotransfer functions.

机构信息

Soil Science and Agricultural Chemistry, Fac. Sciences, Univ. Vigo, 32004, Ourense, Spain.

Soil Science and Agricultural Chemistry, Fac. Sciences, Univ. Vigo, 32004, Ourense, Spain.

出版信息

Ecotoxicol Environ Saf. 2020 Jun 15;196:110584. doi: 10.1016/j.ecoenv.2020.110584. Epub 2020 Apr 8.

Abstract

Tetracycline antibiotics spread in the environment constitute a real threat, causing risks that should be controlled. Retention/release of these compounds after interacting with soil components are the main process governing their entry into water bodies, plant uptake, and availability for soil microorganisms. In this work, batch-type experiments were performed to study adsorption/desorption of oxytetracycline (OTC) and chlortetracycline (CTC) in 63 crop soils. The Freundlich model satisfactory described adsorption curves, showing strong affinity of both antibiotics to soils, with adsorption coefficient (K) values between 1015 and 9733 L μmol kg for OTC, and between 1099 and 11344 L μmol kg for CTC. Desorption percentages were always lower than 10%, indicating that adsorption is highly irreversible. Furthermore, the desorption coefficient (K) correlated positive and significantly with K, showing that those soils characterized by higher adsorption were also those showing less desorption. Soil organic carbon (SOC) was the soil characteristic that most explained the variance of K, both for adsorption and desorption, which caused that soils with higher SOC scores showed higher adsorption and lower desorption for both antibiotics. Pedotransfer functions were developed for OTC and CTC, and resulted effective to satisfactory predict K and K values. These equations would facilitate an easy identification of soils vulnerable to antibiotics pollution, which would allow to program appropriate management practices to decrease undesirable effects on the environment and on public health.

摘要

四环素类抗生素在环境中的传播构成了真正的威胁,带来了需要加以控制的风险。这些化合物与土壤成分相互作用后,其在水体中的迁移、植物吸收和土壤微生物可利用性主要受保留/释放过程的控制。在这项工作中,进行了批量实验,以研究 63 种作物土壤中氧四环素(OTC)和金霉素(CTC)的吸附/解吸。Freundlich 模型很好地描述了吸附曲线,表明两种抗生素对土壤具有很强的亲和力,OTC 的吸附系数(K)值在 1015 和 9733 L μmol kg 之间,CTC 的吸附系数(K)值在 1099 和 11344 L μmol kg 之间。解吸百分比始终低于 10%,表明吸附是高度不可逆的。此外,解吸系数(Kd)与 K 呈正相关且显著相关,表明那些吸附能力较高的土壤,其解吸能力也较低。土壤有机碳(SOC)是最能解释 K 吸附和解吸变异的土壤特性,这导致 SOC 得分较高的土壤对两种抗生素的吸附能力更高,解吸能力更低。针对 OTC 和 CTC 开发了转移函数,结果表明这些函数能够有效地预测 K 和 Kd 值。这些方程将有助于识别易受抗生素污染的土壤,从而可以制定适当的管理措施,减少对环境和公共健康的不利影响。

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