一种测定环境空气中丙烯醛和其他羰基浓度的灵敏方法的开发和应用。

Thomas M Cahill, M Judith Charles, Vincent Y Seaman
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引用次数: 0

摘要

丙烯醛是一种不饱和醛,在最近的环境空气质量评估中已被确定为最重要的有毒空气污染物之一。然而,目前测定丙烯醛浓度的方法灵敏度、选择性和可重复性差。不饱和羰基,特别是丙烯醛的收集和分析,由于不稳定的衍生物、类似化合物的共洗脱和臭氧干扰而变得复杂。本研究的主要目的是开发一种分析方法来测量在短采样周期内获得的环境空气样品中以低万亿分之一浓度存在的丙烯醛和其他挥发性羰基。我们设计的方法使用雾室,其中空气样品中的羰基与亚硫酸盐在雾室溶液中形成水溶性加合物,有效地捕获了溶液中的羰基。雾室方法被证明是有效的,在流速约为17 L/min时,每个雾室对丙烯醛的收集效率至少为70%。样品收集后,羰基通过加入过氧化氢从亚硫酸酯加合物中释放出来,将亚硫酸酯转化为硫酸盐,逆转亚硫酸酯加成反应。然后,游离羰基被o-(2,3,4,5,6-五氟苯基)羟胺(PFBHA*)衍生化,这稳定了分析物,使它们更容易被电子捕获负电离质谱(ECNI-MS)检测到。然后提取衍生物并用气相色谱-质谱(GC-MS)分析。雾室法应用于现场测试,以确定纽约州布法罗和平桥广场附近环境空气中丙烯醛的含量,该地区靠近美国和加拿大之间的主要过境点,交通繁忙。此外,根据职业安全与健康管理局(OSHA)方法52,在该地点同时部署了2-(羟甲基)哌啶(2- hmp)涂层的XAD-2吸附剂盒和基于使用丹酰肼(DNSH)的被动采样器,从而提供了比较方法的机会。雾室结果表明,和平桥交通明显是丙烯醛的来源,在广场下风152.4 m处(东北方向),丙烯醛的平均浓度为0.26微克/立方米。OSHA墨盒被证明对测定环境丙烯醛浓度太不敏感。DNSH被动采样器返回的浓度接近检测极限;因此,该数值略高于雾室结果,且不太一致。然后应用优化的雾室方法测定北加州三个地点的大气丙烯醛浓度:一个地点选择反映半球背景,一个地区以生物源为主,和一个城市环境。测定的丙烯醛平均浓度分别为0.056、0.089和0.290 μ g/m3,检出限为0.012 μ g/m3。野外获得的重复样品一致性较好,相对标准偏差(rsd)在半球背景点为19%,在城市站点为3%。当前雾室法的优点是,它可以在短时间内以足够的灵敏度测定环境丙烯醛浓度,即使在相对“清洁”的环境中也是有效的。这允许测定与丙烯醛浓度相关的时间模式,如反应动力学的日周期。该方法的主要缺点是费力且耗时,并且需要专门的设备,因此难以用于丙烯醛的常规监测。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Development and application of a sensitive method to determine concentrations of acrolein and other carbonyls in ambient air.

Acrolein, an unsaturated aldehyde, has been identified as one of the most important toxic air pollutants in recent assessments of ambient air quality. Current methods for determining acrolein concentrations, however, suffer from poor sensitivity, selectivity, and reproducibility. The collection and analysis of unsaturated carbonyls, and acrolein in particular, is complicated by unstable derivatives, coelution of similar compounds, and ozone interference. The primary objective of this research was to develop an analytical method to measure acrolein and other volatile carbonyls present in low part-per-trillion concentrations in ambient air samples obtained over short sampling periods. The method we devised uses a mist chamber in which carbonyls from air samples form water-soluble adducts with bisulfite in the chamber solution, effectively trapping the carbonyls in the solution. The mist chamber methodology proved effective, with collection efficiency for acrolein of at least 70% for each mist chamber at a flow rate of approximately 17 L/min. After the sample collection, the carbonyls are liberated from the bisulfite adducts through the addition of hydrogen peroxide, which converts the bisulfite to sulfate, reversing the bisulfite addition reaction. The free carbonyls are then derivatized by o-(2,3,4,5,6-pentafluorobenzyl)hydroxylamine (PFBHA*), which stabilizes the analytes and makes them easier to detect by electron-capture negative ionization mass spectrometry (ECNI-MS). The derivatives are then extracted and analyzed by gas chromatography-mass spectrometry (GC-MS). The mist chamber method was applied in a field test to determine the extent of acrolein in ambient air near the Peace Bridge plaza in Buffalo, New York, an area of heavy traffic near a major border crossing between the United States and Canada. In addition, XAD-2 adsorbent cartridges coated with 2-(hydroxymethyl)piperidine (2-HMP) according to Occupational Safety and Health Administration (OSHA) Method 52 and passive samplers based on the use of dansylhydrazine (DNSH) were deployed at this location at the same time, which provided the opportunity to compare methods. The mist chamber results showed that the Peace Bridge traffic was clearly a source of acrolein, with an average concentration of 0.26 microg/m3 at a site 152.4 m downwind (northeast) of the plaza. The OSHA cartridges proved to be too insensitive to determine ambient acrolein concentrations. The DNSH passive samplers returned concentrations near the limit of detection; hence the values were a little higher and less consistent than those in the mist chamber results. The optimized mist chamber method was then applied to determine atmospheric acrolein concentrations at three sites in northern California: a site chosen to reflect the hemispheric background, a region dominated by biogenic sources, and an urban environment. The resulting average acrolein concentrations were 0.056, 0.089, and 0.290 microg/m3, respectively, and the limit of detection was 0.012 microg/m3 The consistency of the replicate samples obtained in the field was good, with the relative standard deviations (RSDs) ranging from 19% at the hemispheric background site to 3% at the urban site. The advantage of the current mist chamber method is that it can determine ambient acrolein concentrations over short time periods with enough sensitivity to be effective even in relatively "clean" environments. This allows for the determination of temporal patterns related to acrolein concentrations, such as diurnal cycles of reaction kinetics. The main disadvantages of the method are that it is laborious and time-consuming and requires specialized equipment that makes it difficult to utilize for routine monitoring of acrolein.

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