Development of a Methodology to Determine Antibiotic Concentrations in Water Samples Using High-Pressure Liquid Chromatography

Tahnee Qualls, C. Agouridis, M. Kulshrestha
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引用次数: 2

Abstract

JYI | June 2017 | Vol. 33 | Issue 1 © Qualls, Agouridis, Kulshrestha 2017 application of manure is the main pathway for veterinary antibiotic introduction into the terrestrial and aquatic environments. In agriculture, antibiotics are used for both therapeutic as well as non-therapeutic purposes. The two main non-therapeutic uses of antibiotics in livestock are growth additives and illness prevention (Shore, & Pruden, 2009). Estimates are that 11 million kg of antibiotics were used in 2002 along for non-therapeutic uses (Davis et al., 2006). Unfortunately, large amounts of administered antibiotics are not metabolized by animals but instead are excreted in manure. Rates of unmetabolized antibiotics are as high 70-90% as in the case of tetracyclines, which are one of the most used classes of antibiotics (Kumar Gupta, Chander, & Singh, 2005; USEPA, 2013). Manures are commonly applied across croplands as part of farm nutrient management plans. Hence, the antibiotics in these manures are land applied as well. Once applied to the land, antibiotics are transported to surface waters, via runoff, or ground waters, through infiltration. To date, only a limited amount of research has been conducted on the transport of antibiotics in the runoff, but this research indicates that the mechanisms of transport vary with antibiotic type. Some antibiotics bind to and are transported with soil, while others do not (Tolls, 2001). Limited studies have examined the use of best management practices (BMPs), such as vegetated filter strips, and the addition of alum to minimize antibiotic transport (Enlow, 2014; DeLaune, & Moore, 2013; Lin et al., 2011). INTRODUCTION The U.S. Environmental Protection Agency (USEPA) classifies antibiotics as a contaminant of emerging concern (CEC) because they are detected in the environment at higher than expected levels and may negatively impact human and aquatic ecosystems (USEPA, 2013). The risk these antibiotics pose to humans and aquatic life is not known; however, the primary concern is that the antibiotic-resistant strains of bacteria will develop. Utilization in human healthcare and livestock care are the two main sources of antibiotics in the environment. Unlike human waste, which is treated via treatment plants or septic systems, livestock waste is oftentimes directly applied to the land as part of a nutrient management plan (NRCS, 2012). Baguer, Jensen, and Krogh (2000) noted that land Development of a Methodology to Determine Antibiotic Concentrations in Water Samples Using High-Pressure Liquid Chromatography
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高压液相色谱法测定水样中抗生素浓度方法的建立
JYI | June 2017 | Vol. 33 | Issue 1©Qualls, Agouridis, Kulshrestha 2017施用粪便是兽医抗生素进入陆地和水生环境的主要途径。在农业中,抗生素既用于治疗目的,也用于非治疗目的。抗生素在牲畜中的两个主要非治疗用途是生长添加剂和疾病预防(Shore, & Pruden, 2009)。据估计,2002年用于非治疗用途的抗生素有1100万公斤(Davis等人,2006年)。不幸的是,大量给药的抗生素没有被动物代谢,而是通过粪便排出体外。与四环素类抗生素一样,未代谢抗生素的使用率高达70-90%,而四环素类抗生素是使用最多的抗生素之一(Kumar Gupta, Chander, & Singh, 2005;构成,2013)。作为农场养分管理计划的一部分,肥料通常在农田中施用。因此,这些粪便中的抗生素也被土地使用。抗生素一旦施用于土地,就会通过径流或渗透进入地表水或地下水。迄今为止,对抗生素在径流中的转运进行的研究数量有限,但本研究表明,转运机制因抗生素类型而异。一些抗生素与土壤结合并随土壤运输,而另一些则没有(Tolls, 2001年)。有限的研究检查了最佳管理实践(BMPs)的使用,例如植物过滤条和添加明矾以减少抗生素运输(Enlow, 2014;DeLaune, & Moore, 2013;Lin et al., 2011)。美国环境保护署(USEPA)将抗生素列为新兴关注污染物(CEC),因为它们在环境中被检测到的水平高于预期,并可能对人类和水生生态系统产生负面影响(USEPA, 2013)。这些抗生素对人类和水生生物造成的风险尚不清楚;然而,主要的担忧是会产生耐抗生素的细菌菌株。人类医疗保健和牲畜护理是环境中抗生素的两个主要来源。与通过处理厂或化粪池系统处理的人类废物不同,牲畜废物通常作为营养管理计划的一部分直接应用于土地(NRCS, 2012)。Baguer, Jensen和Krogh(2000)指出,开发了一种使用高压液相色谱法测定水样中抗生素浓度的方法
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