Department of Civil and Environmental Engineering, Colorado State University, Fort Collins, CO 80523-1372, USA.
J Hazard Mater. 2010 Mar 15;175(1-3):836-43. doi: 10.1016/j.jhazmat.2009.10.086. Epub 2009 Oct 30.
Occurrence of human and veterinary antibiotics has been reported in various environmental compartments. Yet, there is a lack of information verifying the transport mechanisms from source to environment, particularly the transport of veterinary antibiotics as a non-point source pollutant. A rainfall simulation study was conducted to address surface runoff as a possible transport mechanism of veterinary antibiotics introduced in the field and mass balance was calculated with supplementary surface and depth soil measurement. Seven veterinary antibiotics that are the most abundantly used in agriculture for therapeutic and non-therapeutic (growth-promotion) purposes were examined in this study, including tetracycline (TC), chlortetracycline (CTC), sulfathiazole (STZ), sulfamethazine (SMZ), erythromycin (ETM), tylosin (TYL), and monensin (MNS). Runoff in aqueous and sediment phases was collected every 5 min for 1h with varied rainfall intensity and additional surface (0-2 cm) and depth (2-30 cm) soil samples were collected after rainfall simulation for mass balance analysis. Quantification of antibiotic concentration in all collected samples was based on solid phase extraction (SPE) followed by measurement with high-performance liquid chromatography/tandem mass spectrometry (HPLC/MS/MS). MNS showed the highest concentration in runoff aqueous samples (0.22 mg plot(-1)), while ETM showed the highest concentration in runoff sediment samples (0.08 mg plot(-1)). The highest concentration of each applied antibiotic in surface soil samples occurred at different locations. This result might indicate the mobility of these compounds in surface soil varies due to different physicochemical properties among the antibiotics. Further, the analysis results showed that all of the subject antibiotics had penetrated into the subsurface; yet, no residuals were found for STZ, suggesting this compound might have penetrated even deeper into the soil. These results indicate that aqueous or sediment erosion control might reduce the transport of veterinary antibiotics in the environment.
已在各种环境介质中报道了人用和兽用抗生素的存在。然而,对于从源头到环境的传输机制,尤其是作为非点源污染物的兽用抗生素的传输机制,缺乏相关信息。进行了一项降雨模拟研究,以确定地表径流是否是引入田间的兽用抗生素的一种可能传输机制,并通过补充的地表和深度土壤测量来计算质量平衡。本研究检验了 7 种在农业中用于治疗和非治疗(促生长)目的的最广泛使用的兽用抗生素,包括四环素(TC)、金霉素(CTC)、磺胺噻唑(STZ)、磺胺甲噁唑(SMZ)、红霉素(ETM)、泰乐菌素(TYL)和莫能菌素(MNS)。在不同降雨强度下,每 5 分钟收集一次 1 小时的水相和泥沙相径流,并在降雨模拟后收集额外的地表(0-2cm)和深度(2-30cm)土壤样品,以进行质量平衡分析。所有收集样品中抗生素浓度的定量均基于固相萃取(SPE),然后用高效液相色谱/串联质谱(HPLC/MS/MS)进行测量。MNS 在径流水溶液样品中的浓度最高(0.22mg 小区-1),而 ETM 在径流泥沙样品中的浓度最高(0.08mg 小区-1)。表面土壤样品中每种施用药剂的最高浓度出现在不同的位置。这一结果可能表明这些化合物在地表土壤中的移动性因抗生素之间不同的物理化学性质而有所不同。此外,分析结果表明,所有受试抗生素均已渗透到地下,但未检测到 STZ 的残留,表明该化合物可能已渗透到更深的土壤中。这些结果表明,控制水相或泥沙侵蚀可能会减少环境中兽用抗生素的传输。