Sapozhnikova Yelena, Pennington Paul, Wirth Edward, Fulton Michael
JHT Inc., (Contractor to NOAA), 331 Fort Johnson Rd., Charleston, SC 29412, USA.
J Environ Monit. 2009 Apr;11(4):808-14. doi: 10.1039/b818273f. Epub 2009 Feb 6.
Fate and transport of Irgarol 1051 were assessed using a modular estuarine mesocosm containing natural seawater, saltmarsh sediments, marsh grass, shrimp, clams, snails, and naturally derived planktonic and benthic microorganisms. The mesocosms were enclosed in a greenhouse under near ambient conditions, and included a saltwater sump and a simulated tidal flux. The exposure was comprised of four replicate treatments of 0, 100, 1,000 and 10,000 ng/L Irgarol. Solid-phase extraction (SPE) was used to extract Irgarol and its major metabolite M1 (aka GS26575) from water samples. Sediment samples were extracted using Accelerated Solvent Extraction (ASE) with 100% dichloromethane. Irgarol and M1 were separated and quantified utilizing Liquid Chromatography Tandem Mass Spectrometry (LC-MS-MS) with ElectroSpray Ionization in Multiple Reaction Monitoring mode. Aqueous concentrations of Irgarol declined rapidly (average 93% loss) over the course of the 35 day experiment while Irgarol was accumulated in the sediments (average mass balance of 75 +/- 5%). Loss of aqueous Irgarol occurred in two distinct phases, a relatively rapid phase up to 96 hours post-dose, and a slower phase following 96 hours. The rate constants of the initial rapid degradation phase (k(1)) for treatments 100 and 1,000 ng/L Irgarol were 2-3 times higher than the rate constants of the subsequent slow degradation phase (k(2)) for these treatments. The average half-life of Irgarol in water was 7 +/- 3 days. The aqueous concentration of Irgarol's metabolite, M1 increased over the course of the experiment. By 35 days post-dose, M1 concentrations in water averaged about 3% of the parent compound. M1 also accumulated in mesocosm sediments (average 16.7 +/- 2.5% of total Irgarol dose). Mass balance calculations showed that by 35 days, Irgarol and M1 amounts in mesocosm water and sediments were close to 100% of the initial Irgarol dose. Average partition coefficient normalized for organic carbon (log K(oc)) calculated for Irgarol was 3.2 +/- 0.1 for 35 days post-dose. Accumulation of Irgarol and M1 in mesocosm sediments may warrant further study to assess toxicity for benthic communities.
使用一个模块化河口围隔生态系统评估了烯啶虫胺1051的归宿和迁移,该围隔生态系统包含天然海水、盐沼沉积物、沼泽草、虾、蛤、蜗牛以及天然来源的浮游和底栖微生物。围隔生态系统封闭在温室中,处于接近自然的条件下,包括一个盐水贮槽和模拟潮汐通量。暴露处理包括0、100、1000和10000 ng/L烯啶虫胺的四个重复处理组。采用固相萃取(SPE)从水样中提取烯啶虫胺及其主要代谢物M1(即GS26575)。沉积物样品采用100%二氯甲烷加速溶剂萃取(ASE)进行提取。利用液相色谱串联质谱(LC-MS-MS)在多反应监测模式下通过电喷雾电离对烯啶虫胺和M1进行分离和定量。在35天的实验过程中,烯啶虫胺的水体浓度迅速下降(平均损失93%),而烯啶虫胺在沉积物中积累(平均质量平衡为75±5%)。水体中烯啶虫胺的损失分为两个不同阶段:给药后96小时内相对较快的阶段和96小时后的较慢阶段。对于100和1000 ng/L烯啶虫胺处理组,初始快速降解阶段(k(1))的速率常数比这些处理组后续缓慢降解阶段(k(2))的速率常数高2 - 3倍。烯啶虫胺在水中的平均半衰期为7±3天。烯啶虫胺代谢物M1的水体浓度在实验过程中有所增加。给药后35天,水中M1浓度平均约为母体化合物的3%。M1也在围隔生态系统沉积物中积累(平均占烯啶虫胺总剂量的16.7±2.5%)。质量平衡计算表明,到35天时围隔生态系统水体和沉积物中烯啶虫胺和M1的量接近初始烯啶虫胺剂量的100%。给药后35天计算得出烯啶虫胺的平均有机碳归一化分配系数(log K(oc))为3.2±0.1。烯啶虫胺和M1在围隔生态系统沉积物中的积累可能需要进一步研究以评估对底栖生物群落的毒性。