Centre for Toxicology, School of Environmental Sciences, University of Guelph, Guelph, ON N1G 2W1, Canada.
Laboratory Services Division, University of Guelph, Guelph, ON N1G 2W1, Canada.
Sci Total Environ. 2016 Apr 15;550:449-458. doi: 10.1016/j.scitotenv.2016.01.140. Epub 2016 Feb 2.
This study optimized existing analytical approaches and characterized the effect of sediment total organic carbon (0.05-2.05% TOC), and water depth (15, 30, and 90cm) on the fate of MON 0818, a commercial mixture of polyoxyethylene amine surfactants (POEAs), in outdoor microcosms. Mixtures of POEAs are commonly used as adjuvants in commercial herbicide formulations containing glyphosate. Until recently, analytical methods sensitive enough to monitor environmental concentrations of POEAs in aquatic systems were not available. After optimizing recently developed analytical methods, we found that the combined use of accelerated solvent extraction (ASE) and liquid chromatography-tandem mass spectrometry provided a reliable approach for determining the concentration of sediment-adsorbed POEAs. The surfactant showed strong affinity for sediment materials, with low maximum recoveries by ASE of 52%. Under microcosm conditions, water depth or sediment characteristics did not significantly affect the water-column half-life of POEA, which ranged from 3.2 to 5.3h. Binding of POEAs to suspended solids was observed, which dissipated via one- or two-phase exponential decay; when two-phase decay occurred, fast phase half-life values ranged from 0.71 to 1.3h and slow-phase values ranged from 18 to 44h. Concentrations of POEA increased in sediment shortly after application and decreased over the study period with a half-life of 5.8 to 71d. The concentrations of POEAs in the sediment of the shallow (15cm) ponds dissipated following a two-phase exponential decay model with an initial fast-phase half-life of 1.1 to 8.9d and a slower second-phase half-life of 21d. Our results suggest that aquatic organisms are unlikely to be exposed to POEAs in aqueous phase for periods of more than a few hours following an over-water application, and that sediment is a significant sink for POEAs in aquatic systems.
本研究优化了现有的分析方法,并研究了沉积物总有机碳(0.05-2.05% TOC)和水深(15、30 和 90cm)对商业聚氧乙烯胺表面活性剂(POEAs)混合物 MON 0818 在户外微宇宙中归宿的影响。POEAs 混合物通常用作含有草甘膦的商业除草剂制剂的助剂。直到最近,还没有足够灵敏的分析方法来监测水生系统中 POEAs 的环境浓度。在优化了最近开发的分析方法后,我们发现加速溶剂萃取(ASE)和液相色谱-串联质谱的联合使用为确定沉积物中吸附的 POEAs 浓度提供了可靠的方法。该表面活性剂对沉积物材料具有很强的亲和力,ASE 的最大回收率仅为 52%。在微宇宙条件下,水深或沉积物特性对 POEA 的水相半衰期没有显著影响,半衰期范围为 3.2-5.3h。观察到 POEAs 与悬浮固体结合,并通过单相或两相指数衰减消散;当发生两相衰减时,快相半衰期值范围为 0.71-1.3h,慢相半衰期值范围为 18-44h。POEA 浓度在施用后不久即增加,并在研究期间减少,半衰期为 5.8-71d。浅水(15cm)池塘沉积物中 POEAs 的浓度遵循两相指数衰减模型,初始快相半衰期为 1.1-8.9d,较慢的第二相半衰期为 21d。我们的结果表明,在水上施药后,水生生物在几小时内不太可能暴露于 POEAs 的水相中,而沉积物是水生系统中 POEAs 的重要汇。