Agriculture and Agri-Food Canada, Research Centre, 107 Science Place, Saskatoon, SK, S7N 0X2, Canada.
Toxicology Graduate Program, Univ. of Saskatchewan, Saskatoon, SK, S7N 5B3, Canada.
J Environ Qual. 2020 Sep;49(5):1435-1444. doi: 10.1002/jeq2.20079. Epub 2020 Aug 4.
Chlortetracycline (CTC), an antimicrobial administered as a feed additive to cattle, swine, and poultry, is present in the corresponding manure. Land application of raw or processed (composted or stockpiled) manure provides a mechanism by which CTC (and other antimicrobials) enters the environment and becomes available for transport to surface receiving waters via rainfall or snowmelt runoff. Chlortetracycline has been detected in Canadian surface waters, but little has been reported on its fate in aquatic ecosystems. To address this knowledge gap, the dissipation of CTC-enol was monitored in deionized water and water typical of wetlands within the prairie region of Canada. In deionized water, CTC-enol tautomerized to CTC-keto, and both tautomers epimerized to 4-epi-CTC-enol and 4-epi-CTC-keto, respectively. Irreversible isomerization to iso-CTC occurred, which then epimerized to 4-epi-iso-CTC. In wetland water, although tauterization of CTC-enol to CTC-keto occurred, there was no evidence of the formation of the 4-epimers of either CTC-enol or CTC-keto. The major product formed in the wetland water was iso-CTC, some of which epimerized to 4-epi-iso-CTC. Although CTC-enol was shown to tautomerize to CTC-keto, the concentration of CTC-keto remained low in both deionized and wetland water, suggesting that the isomerization of CTC-enol to iso-CTC most likely occurred via CTC-keto. The dissipation of CTC-enol in wetland water was described by pseudo first-order kinetics with a DT (time required for 50% dissipation) value of 4.8 h. The short DT value of CTC and reduced antimicrobial activity of iso-CTC and 4-epi-iso-CTC suggest a lower probability for selection for CTC-resistant bacteria in Canadian Prairie aquatic ecosystems.
金霉素(CTC)是一种作为饲料添加剂用于牛、猪和家禽的抗菌药物,存在于相应的粪便中。生粪肥或经过处理(堆肥或储存)的粪肥的土地应用为 CTC(和其他抗菌药物)进入环境并通过降雨或融雪径流可用于向地表接受水体迁移提供了一种机制。已经在加拿大地表水检测到金霉素,但有关其在水生生态系统中的命运的报道很少。为了解决这一知识空白,监测了去离子水和加拿大草原地区湿地典型水中的 CTC-烯醇的消散情况。在去离子水中,CTC-烯醇互变异构化为 CTC-酮,两种互变异构体分别差向异构化为 4-表-CTC-烯醇和 4-表-CTC-酮。然后发生不可逆的异构化为 iso-CTC,然后差向异构化为 4-表-iso-CTC。在湿地水中,尽管 CTC-烯醇发生互变异构化为 CTC-酮,但没有形成 CTC-烯醇或 CTC-酮的 4-差向异构体的证据。在湿地水中形成的主要产物是 iso-CTC,其中一些差向异构化为 4-表-iso-CTC。尽管 CTC-烯醇被证明可以互变异构化为 CTC-酮,但 CTC-酮在去离子水和湿地水中的浓度都很低,这表明 CTC-烯醇向 iso-CTC 的异构化很可能通过 CTC-酮发生。用拟一级动力学描述了 CTC-烯醇在湿地水中的消散,DT(50%消散所需的时间)值为 4.8 h。在加拿大草原水生生态系统中,金霉素的 DT 值较短,以及 iso-CTC 和 4-表-iso-CTC 的抗菌活性降低,这表明选择金霉素抗性细菌的可能性较低。