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A serial PFASs sorption technique coupled with adapted high volume direct aqueous injection LCMS method

机译:一种串联压粉吸收技术,耦合,适应大容量直接水 - 注射LCMS方法

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Per- and polyfluoroalkyl substances (PFAS) are ubiquitous global environmental contaminants, environmentally persistent, mobile, can bioaccumulate and are toxic. Increasing emphasis is placed on the immobilisation and removal of PFAS from contaminated environmental matrices such as: potable water, surface water, groundwater, wastewater, sediments and soils (Dauchy et al., 2017; Cao et al., 2019; Hepburn et al., 2019). To achieve this, development of PFAS sorbents is increasingly undertaken (Du et al., 2014). Sorption studies are used to observe the interaction of sorbent and sorbate, but have two key limitations when undertaking sorption experiments for PFAS (1) the experimental protocol and (2) analytical techniques. The current batch sorption methods approached recommended by OECD Guideline 106 (OECD, 2000) are problematic, firstly, due to large sample numbers and PFAS specific laboratory difficulties, including near ubiquitous background PFAS contamination. Secondly, PFAS analytical techniques currently require solid-phase extraction (SPE) to be employed, which is slow and expensive, prior to instrumental analysis with liquid chromatography-mass spectrometry (LC-MS). A suitable alternative approach is needed to mitigate the drawbacks of current methodologies whilst catering for the high sample throughput required by benchtop trials characterising the sorption behaviour of PFAS - sorbent pairings.?A suitable method for PFAS measurement, overcoming shortcomings of current batch sorption methodologies is presented?The method can be applied to a wide range of sorbents and sorption environment conditions associated with PFAS immobilisation or removal in the environment?The presented method is novel through its high sample throughput, simple approach and minimisation of cross contamination sources.
机译:普遍存在的全球环境污染物(PFAS),无害环境持久性,移动,可以生物累积和有毒。从污染的环境基质中,增加重点并从污染的环境基质中除去PFA,如:饮用水,地表水,地下水,废水,沉积物和土壤(Dauchy等,2017; Cao等,2019; Hepburn等。 ,2019)。为实现这一目标,越来越多地进行PFAS吸附剂的发展(Du等人,2014)。吸附研究用于观察吸附剂和山梨酸盐的相互作用,但是在对PFAs(1)的吸附实验进行实验方案和(2)分析技术时具有两个关键限制。经合组织指南106(OECD,2000)推荐的当前批量吸附方法是有问题的,首先是由于众多样品数和PFA特定的实验室困难,包括普遍存在的背景PFAS污染。其次,PFAS分析技术目前需要采用固相萃取(SPE),在液相色谱 - 质谱(LC-MS)仪器分析之前,在仪器分析之前,这是缓慢且昂贵的。需要一种合适的替代方法来减轻当前方法的缺点,而抚慰性的基础试验表征PFAS的吸附行为的高样品产量,同时迎合PFAS - 吸附剂配对的吸附行为。适用于PFAS测量的合适方法,克服了当前分批吸附方法的缺点是呈现了吗?该方法可以应用于各种吸附剂和吸附环境条件,与PFA固定或在环境中移除相关的含量,通过其高样本吞吐量,简单的方法和交叉污染来源的最小化的方法是新颖的。

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