浙江农业学报

• 环境科学 • 上一篇    下一篇

磺胺类药物在渔业沉积物中的降解及其影响因素

  

  1. (上海市水产研究所,上海 200433)
  • 出版日期:2016-04-25 发布日期:2016-04-27

Degradation behavior of sulfonamides in aquaculture sediments and its influencing factors

  1. (Shanghai Fisheries Research Institute, Shanghai 200433, China)
  • Online:2016-04-25 Published:2016-04-27

摘要: 为评价磺胺类药物在渔业沉积物中的降解行为,选择渔业沉积物中检出率较高的磺胺嘧啶(SD)、磺胺二甲基嘧啶(SM2)和磺胺甲恶唑(SMZ)为研究对象,采用室内模拟实验,研究不同环境因素(温度、微生物、光照及初始浓度等)对其在渔业沉积物中降解的影响。结果表明,提高温度可以有效促进SD,SM2和SMZ在沉积物中的降解,25 ℃和35 ℃培养条件下比5 ℃培养条件下有更高的降解率。SD和SM2在沉积物中主要以非生物降解为主,微生物降解为辅。SMZ在沉积物中受微生物降解影响显著,微生物降解的贡献率为55%。光照对沉积物中3种磺胺类药物降解无显著影响。随着初始浓度的增加,降解效率逐步下降,半衰期延长。在低浓度(0.01和0.1 mg·kg-1)时,SD,SM2和SMZ的半衰期较短;当初始浓度为1~50 mg·kg-1时,SD,SM2和SMZ的半衰期在11.13~128.36 d之间。

关键词: 渔业沉积物, 磺胺, 降解

Abstract: To evaluate the degradation of sulfonamides in aquaculture sediments, sulfadiazine (SD), sulfamethazine (SM2) and sulfamethoxazole (SMZ) which exhibited relatively high detection rates in aquaculture sediments were chosen as the research objects. Through laboratory simulation degradation experiment, a series of environment factors including temperature, microorganism, illumination and initial concentrations in sediments were tested to determine their impacts on degradation of SD, SM2 and SMZ. It was shown that raising temperature could effectively promote the degradation of SD, SM2 and SMZ in sediments, and these sulfonamides exhibited e a higher degradation rate under 25 ℃ and 35 ℃ than that under 5 ℃. SD and SM2 degradation in sediments were mainly attributed to abiotic degradation, and microbial degradation was complementary. SMZ in sediments was significantly influenced by microbial degradation, and the contribution rate of microbial degradation reached 55%. Illumination had no significant effect on the degradation of the three kinds of sulfa drugs in sediments. With the increase of the initial concentrations, the degradation efficiency of SD, SM2 and SMZ declined gradually, and the halflife period of degradation was extended. Under the condition of the lower concentration as 0.01 and 0.1 mg·kg-1, the halflife period of SD, SM2 and SMZ was short. Within the initial concentration of 1~50 mg·kg-1, the halflife period of SD, SM2 and SMZ was 11.13~128.36 d.

Key words: aquaculture sediments, sulfonamides, degradation