Chee-Sanford Joanne C, Mackie Roderick I, Koike Satoshi, Krapac Ivan G, Lin Yu-Feng, Yannarell Anthony C, Maxwell Scott, Aminov Rustam I
USDA-ARS, 1102 S. Goodwin Ave., Urbana, IL 61801, USA.
J Environ Qual. 2009 Apr 27;38(3):1086-108. doi: 10.2134/jeq2008.0128. Print 2009 May-Jun.
Antibiotics are used in animal livestock production for therapeutic treatment of disease and at subtherapeutic levels for growth promotion and improvement of feed efficiency. It is estimated that approximately 75% of antibiotics are not absorbed by animals and are excreted in waste. Antibiotic resistance selection occurs among gastrointestinal bacteria, which are also excreted in manure and stored in waste holding systems. Land application of animal waste is a common disposal method used in the United States and is a means for environmental entry of both antibiotics and genetic resistance determinants. Concerns for bacterial resistance gene selection and dissemination of resistance genes have prompted interest about the concentrations and biological activity of drug residues and break-down metabolites, and their fate and transport. Fecal bacteria can survive for weeks to months in the environment, depending on species and temperature, however, genetic elements can persist regardless of cell viability. Phylogenetic analyses indicate antibiotic resistance genes have evolved, although some genes have been maintained in bacteria before the modern antibiotic era. Quantitative measurements of drug residues and levels of resistance genes are needed, in addition to understanding the environmental mechanisms of genetic selection, gene acquisition, and the spatiotemporal dynamics of these resistance genes and their bacterial hosts. This review article discusses an accumulation of findings that address aspects of the fate, transport, and persistence of antibiotics and antibiotic resistance genes in natural environments, with emphasis on mechanisms pertaining to soil environments following land application of animal waste effluent.
抗生素被用于畜牧生产,用于疾病的治疗,以及以亚治疗剂量促进生长和提高饲料效率。据估计,约75%的抗生素未被动物吸收,而是随粪便排出。抗生素耐药性选择发生在胃肠道细菌中,这些细菌也随粪便排出并储存在粪便储存系统中。在美国,将动物粪便施用于土地是一种常见的处置方法,也是抗生素和耐药基因进入环境的一种途径。对细菌耐药基因选择和耐药基因传播的担忧引发了人们对药物残留及其分解代谢物的浓度、生物活性以及它们的归宿和迁移的兴趣。粪便细菌在环境中可存活数周至数月,具体取决于细菌种类和温度,然而,基因元件无论细胞活力如何都能持续存在。系统发育分析表明抗生素耐药基因已经进化,尽管有些基因在现代抗生素时代之前就已存在于细菌中。除了了解基因选择、基因获得的环境机制以及这些耐药基因及其细菌宿主的时空动态外,还需要对药物残留和耐药基因水平进行定量测量。这篇综述文章讨论了一系列研究结果,这些结果涉及抗生素和抗生素耐药基因在自然环境中的归宿、迁移和持久性,重点是动物粪便废水施用于土地后与土壤环境相关的机制。