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5.1x00a0;This test method has been developed by the US EPA Region 5 Chicago Regional Laboratory (CRL).
5.2x00a0;PFCs are widely used in various industrial and commercial products; they are persistent, bio-accumulative, and ubiquitous in the environment. PFCs have been reported to exhibit developmental toxicity, hepatotoxicity, immunotoxicity, and hormone disturbance. A draft Toxicological Profile for Perfluoroalkyls from the U.S. Department of Health and Human Services is available.7 PFCs have been detected in soils, sludges, surface and drinking waters. Hence, there is a need for quick, easy, and robust method to determine these compounds at trace levels in various soil matrices for understanding of the sources and pathways of exposure.
5.3x00a0;This method has been used to determine selected perfluorinated compounds in sand (Table 4) and four ASTM reference soils (Table 5).
1.1x00a0;This procedure covers the determination of selected perfluorinated compounds (PFCs) in a soil matrix using solvent extraction, filtration, followed by liquid chromatography (LC) and detection with tandem mass spectrometry (MS/MS). These analytes are qualitatively and quantitatively determined by this method. This method adheres to multiple reaction monitoring (MRM) mass spectrometry. This procedure utilizes a quick extraction and is not intended to generate an exhaustive accounting of the content of PFCs in difficult soil matrices. An exhaustive extraction procedure for polyfluoralkyl substances, such as published by Washington et al.2, for difficult matrices should be considered when analyzing PFCs.
1.2x00a0;Unitsx2014;The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.
1.3x00a0;The Method of Detection Limit3 and Reporting Range4 for the target analytes are listed in Table 1.
1.3.1x00a0;The reporting limit in this test method is the minimum value below which data are documented as non-detects. Analyte detections between the method detection limit and the reporting limit are estimated concentrations and are not reported following this test method. In most cases, the reporting limit is calculated from the concentration of the Level 1 calibration standard as shown in Table 2 for the perfluorinated compounds after taking into account a 2 g sample weight and a final extract volume of 10 mL, 508201;% water/508201;% MeOH with 0.18201;% acetic acid. The final extract volume is assumed to be 10 mL because 10 mL ......
然而,這些檢測方法都有一個靈敏度低的缺點。串聯液相色譜 - 質譜聯用(LC/MS/MS)具有高選擇性與靈敏度,因此,是測定生物和環境樣品中全氟烷基表面活性劑含量的最常用的分析方法。13 ?? 在液相色譜 - 質譜 / 質譜聯用(LC/MS/MS)分析之前實施固相萃取(SPE)程序是從水性環境基質中提取全氟烷基表面活性 劑 的 最 常 用 方 法 之 一。...
相關標準目前涉及PFAS的檢測標準很多,主要有美國國家環境保護局(U.S.EPA)的Method 537.1和ASTMD 7979-17、歐盟的《歐盟水框架指令》、中國國標《GB5749-2006生活飲用水衛生標準》、《DB32/T4004-2021 水中17種全氟化合物的測定高效液相色譜串聯質譜法》、《GB/T23243-2009 食品包裝材料中全氟辛烷磺酰基化合物(PFOS)的測高效液相色譜-串聯質譜法...
本實驗參考《超高效液相色譜-新型串聯四極桿質譜法測定環境水體與土壤中的全氟辛酸和全氟辛烷磺酸》,利用萊伯泰科SPE 1000全自動固相萃取系統和MultiVap-10定量平行濃縮儀進行相關方法研究。?...
前言? ? ? 近年來,全氟化合物的毒性檢測研究已成為眾多科研工作者關注的熱點,歐盟、美國、加拿大相繼出臺了一系列環境中全氟化合物的檢測標準。2022年2月,國務院發布第三次全國土壤普查文件,全氟化合物納入本次普查監管范疇。? ? ? 本文使用譜育科技?EXPEC 5210 超高效液相色譜-三重四極桿串聯質譜儀(LC-MS/MS),建立了土壤中全氟辛磺酸和全氟辛酸的殘留量檢測方法。...
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