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Frit inlet/frit outlet flow field-flow fractionation: methodology for colored dissolved organic material in natural waters

机译:玻璃料入口/玻璃料出口流场流分馏:天然水中有色溶解有机物的方法

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Results from the first application FIFO-F1FFF (1 frit inlet/frit outlet-flow field-flow fractionation) to the characterization of colored dissolved organic material (CDOM0 in river and coastal waters are described. F1FFF separates compounds based on their diffusional characteristics. The frit inlet/frit outlet (FIFO) feature was recently developed to concentrate samples inside the F1FFF channel for improved stability, reproducibility and sensitivity. Our results show that FIFO increases sensitivity by an order of magnitude and the system has a linear response to molecualr weight and concentration over a wide dynamic range. Errors for replicate analyses with a Caloosahatchee River sample from southwest Florida were <2.5% for retention time and <4% for peak areas, indicating good reproducibility and precision for the analysis of CDOM in natural water samples. However, recovery rates were low (35-65% for fresh waters and 5.7-8.1% for marine waters) and it will be necessary to test different membranes and lower molecular weight cut-off to improve recoveries in future studies. Molecualr weights were calculated from the measured retention times and log-linear calibration curves generated with polystyrene sulfonate standards (1800-35,000 Da). In river water, approx98% of CDOMoccurred in a fraction centered around 2 kDa and approx2% in a fraction with a maximum at 13 kDa (based on maximum peak intensity for absorbance at 330 nm and fluorescence at 350-450 nm). This minor higher molecular weight fraction was completely gone in offshore coastal waters. This loss may be due to dilution of the river samples and/or biological and photochemical degradation of CDOM.Irradiating a rive sample with sunlight produced a fractogram characteristic of marine waters, suggesting that photodegradation is an important mechanism in altering the molecular and optical characteristics of CDOM.
机译:描述了从首次应用FIFO-F1FFF(玻璃料入口/玻璃料出口流场流分馏)到有色溶解有机物质(河水和沿海水域中的CDOM0)表征的结果,F1FFF根据化合物的扩散特征对其进行分离。玻璃料入口/玻璃料出口(FIFO)功能是最近开发的,用于将样品浓缩在F1FFF通道内,从而提高了稳定性,可重复性和灵敏度,我们的结果表明FIFO将灵敏度提高了一个数量级,并且系统对分子重量和分子量具有线性响应。佛罗里达西南的Caloosahatchee River样品的重复分析保留时间<2.5%,峰面积<4%,这表明天然水样品中CDOM的重现性和精密度很高。 ,回收率很低(淡水为35-65%,海水为5.7-8.1%),因此有必要测试不同nt膜和较低的分子量截留值可提高回收率,以备将来研究之用。由测得的保留时间和聚苯乙烯磺酸盐标准品(1800-35,000 Da)产生的对数线性校准曲线计算分子量。在河水中,约98%的CDOM发生在以2 kDa为中心的馏分中,而约2%的发生在以13 kDa为最大值的馏分中(基于330 nm处的吸光度和350-450 nm处的荧光的最大峰强度)。这种较小的较高分子量部分在沿海近海完全消失了。这种损失可能是由于河流样品的稀释和/或CDOM的生物和光化学降解引起的。用阳光照射河岸样品会产生海水的分形特征,这表明光降解是改变CDOM分子和光学特性的重要机制。 CDOM。

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