...
首页> 外文期刊>Journal of chromatography, A: Including electrophoresis and other separation methods >Effect of seawater salinity on pore-size distribution on a poly(styrene)-based HP20 resin and its adsorption of diarrhetic shellfish toxins
【24h】

Effect of seawater salinity on pore-size distribution on a poly(styrene)-based HP20 resin and its adsorption of diarrhetic shellfish toxins

机译:海水盐度对聚苯乙烯基HP20树脂孔径分布及其对腹泻性贝类毒素的吸附的影响

获取原文
获取原文并翻译 | 示例

摘要

In the present study, okadaic acid (OA) and dinophysistoxin-1 (DTX1) were spiked into artificial seawater at low, medium and high estuarine salinities (9 parts per thousand, 13.5 parts per thousand and 27 parts per thousand). Passive samplers (HP2O resin) used for solid phase adsorption toxin tracking (SPATT) technology were exposed in these seawaters for 12-h periods. Adsorption curves well fitted a pseudo-secondary kinetics model. The highest initial sorption rates of both toxins occurred in the seawater of medium salinity, followed by seawater of low and high estuarine salinity. Pore volumes of micropores (<2 nm) and small mesopores (2 nm < diameter <10 nm) of HP2O resin decreased after adsorption of toxins in seawater at high and low salinity but not in seawater at medium salinity, which demonstrated that the toxin molecules entered into micropores and mesopores (below 10 nm in size) in seawaters of high and low salinity. More toxin or other matrix agglomerates were displayed on the surface of resin deployed in the seawater of medium salinity. Taking into consideration the pore-size distribution and surface images, it appears that intra-particle diffusion governs toxin adsorption in seawater at high salinity while film diffusion mainly controls the adsorption process in seawater at medium salinity. This is the first study to confirm that molecules of OA and DTX1 are able to enter into micropores (<2 nm) and small mesopores (2-10 nm) of HP2O resin in estuarine seawater with high salinity (similar to 27%.). (C) 2014 Elsevier B.V. All rights reserved.
机译:在本研究中,冈田酸(OA)和dinophysistoxin-1(DTX1)被添加到低,中和高河口盐度(千分之9,千分之13.5和千分之27)的人工海水中。将用于固相吸附毒素跟踪(SPATT)技术的被动采样器(HP2O树脂)暴露在这些海水中12小时。吸附曲线很好地拟合了伪二次动力学模型。两种毒素的最高初始吸附率发生在中等盐度的海水中,其次是低和高河口盐度的海水。在高盐度和低盐度的海水中吸附毒素后,HP2O树脂的微孔(<2 nm)和小中孔(2 nm <直径<10 nm)的孔体积减少,但在中盐度的海水中吸附后没有减少,这表明毒素分子在高盐度和低盐度的海水中进入微孔和中孔(尺寸小于10 nm)。在中等盐度海水中部署的树脂表面显示出更多的毒素或其他基质团聚体。考虑到孔径分布和表面图像,似乎颗粒内扩散控制着高盐度海水中的毒素吸附,而膜扩散主要控制着中等盐度海水中的吸附过程。这是第一个证实OA和DTX1分子能够进入高盐度(约27%)的河口海水中的HP2O树脂的微孔(<2 nm)和小的中孔(2-10 nm)的研究。 (C)2014 Elsevier B.V.保留所有权利。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号