机动车辆纳米颗粒的选择性检测和表征。

Murray V Johnston, Joseph P Klems, Christopher A Zordan, M Ross Pennington, James N Smith
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As the distance or transit time from emission to sampling increased, the size distribution shifted to a larger particle size, which confirmed the source assignments. To determine the distribution of emissions from individual vehicles, we correlated camera images with the spike contribution to particle number concentration at each time point. A small percentage of motor vehicles were found to emit a disproportionally large concentration of nanoparticles, and these high emitters included both spark-ignition (SI) and heavy-duty diesel (HDD) vehicles. In addition to characterizing the contribution of the spikes (local sources) to the ambient number concentration, we developed a method to determine the net contribution of motor vehicles (all sources) to the total mass concentration of ambient nanoparticles. 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引用次数: 0

摘要

大量研究表明,接触机动车尾气会增加高危人群心脏病发作、哮喘发作和住院的几率。然而,虽然许多研究都集中在高速公路附近的环境纳米粒子的测量上,但它们并没有集中在特定的道路水平领域,比如人口中心附近的十字路口。在这些地点,观察到颗粒数浓度的非常强烈的峰值。这些峰值与机动车活动有关,并有可能大幅增加接触。表征这些峰值的贡献和组成对于制定暴露模型和减排策略至关重要。为了确定颗粒峰值对环境数字浓度的贡献,我们实施了基于小波的算法,从2009年夏天和冬天在特拉华州威尔明顿采集的测量数据中分离出颗粒峰值。威尔明顿靠近一个每天约有28,000辆汽车通过的道路交叉口。这些测量包括凝结粒子计数器(CPC*)每秒记录一次的数量浓度和大小分布;TSI, Inc., St. Paul, MN)和快速迁移度粒度仪(FMPS)。信号的高频部分,由数浓度的一系列突变尖峰组成,其长度从几秒到几十秒不等,占每日环境数浓度的3%至35%,尖峰贡献有时大于小时数浓度的50%。当数据按颗粒体积加权时,这部分信号对空气动力学直径<或= 0.1微米的颗粒物(PM)的日浓度(PM0.1)的平均贡献为10%至20%。观察颗粒浓度峰值的首选地点是在测量地点周围,在那里,汽车在红灯变绿后加速。随着从发射到采样的距离或传输时间的增加,粒径分布向更大的粒径偏移,这证实了源的分配。为了确定单个车辆的排放分布,我们将相机图像与每个时间点的峰值对颗粒数浓度的贡献相关联。一小部分机动车被发现排放出不成比例的高浓度纳米颗粒,这些高排放者包括火花点火(SI)和重型柴油(HDD)车辆。除了表征峰值(局部源)对环境粒子浓度的贡献外,我们还开发了一种方法来确定机动车辆(所有源)对环境纳米粒子总质量浓度的净贡献。为此,我们将峰值浓度与纳米气溶胶质谱仪(NAMS)测量的纳米颗粒化学成分的快速变化相关联;由约翰斯顿集团建造)。NAMS用高能激光脉冲照射单个大小选择的纳米颗粒,产生由多个带电原子离子组成的质谱。每个粒子的元素组成是由每个元素的离子信号强度确定的。然而,重叠的质量电荷比(m/z)在4 m/z (O(+4)和C(+3))和8 m/z (O(+2)和S(+4))需要分离成它们的组成离子,以获得代表性的组成。为此,我们开发了一种方法,以蔗糖和硫酸铵[(NH4)2SO4]作为校准标准,对这些离子信号进行反卷积。使用这种方法,对于各种测试颗粒,碳(C)、氧(O)、氮(N)和硫(S)的期望和测量的元素摩尔分数之间的差异通常远小于10%。发现周围的纳米颗粒主要由碳、氧、氮和硫组成。许多颗粒还含有硅(Si)。元素组成被划分为大气气溶胶中常见的分子种类:硫酸盐(SO4(2-))、硝酸盐(NO3-)、铵(NH4+)、碳质物质,当存在时,还有二氧化硅(SiO2)。将NAMS化学成分测量与峰值贡献相关联,可以建立代表机动车排放的化学概况,可用于分摊它们对环境纳米颗粒质量的总贡献。来自机动车的颗粒物主要由未氧化的碳质物质组成,而非机动车颗粒物主要由SO42-、NO3-和氧化的碳质物质组成。在冬季测量期间,机动车分别贡献了48%和60%的纳米颗粒质量和数量浓度,而在夏季测量期间,机动车分别只贡献了16%和49%的纳米颗粒质量和数量浓度。 通过将每个时间点的静态相机图像、化学成分和峰值贡献相关联,估计了SI与HDD载体的化学成分概况和对纳米颗粒质量浓度的贡献。SI和HDD车辆的总质量贡献大致相等,但分割的不确定性很大。本研究的结果表明,纳米颗粒浓度在路口附近比在同一条道路上更高,但离路口更远。减少机动车辆对环境纳米颗粒物质贡献的可能方法包括尽量减少十字路口的走走停停活动(即,红灯变绿后加速的车辆),以及识别一小部分排放不成比例的大量纳米颗粒的机动车辆。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Selective detection and characterization of nanoparticles from motor vehicles.

Numerous studies have shown that exposure to motor vehicle emissions increases the probability of heart attacks, asthma attacks, and hospital visits among at-risk individuals. However, while many studies have focused on measurements of ambient nanoparticles near highways, they have not focused on specific road-level domains, such as intersections near population centers. At these locations, very intense spikes in particle number concentration have been observed. These spikes have been linked to motor vehicle activity and have the potential to increase exposure dramatically. Characterizing both the contribution and composition of these spikes is critical in developing exposure models and abatement strategies. To determine the contribution of the particle spikes to the ambient number concentration, we implemented wavelet-based algorithms to isolate the particle spikes from measurements taken during the summer and winter of 2009 in Wilmington, Delaware, adjacent to a roadway intersection that approximately 28,000 vehicles pass through daily. These measurements included both number concentration and size distributions recorded once every second by a condensation particle counter (CPC*; TSI, Inc., St. Paul, MN) and a fast mobility particle sizer (FMPS). The high-frequency portion of the signal, consisting of a series of abrupt spikes in number concentration that varied in length from a few seconds to tens of seconds, accounted for 3% to 35% of the daily ambient number concentration, with spike contributions sometimes greater than 50% of hourly number concentrations. When the data were weighted by particle volume, this portion of the signal contributed an average of 10% to 20% to the daily concentration of particulate matter (PM) < or = 0.1 microm in aerodynamic diameter (PM0.1). The preferred locations for observing particle concentration spikes were those surrounding the measurement site at which motor vehicles accelerated after a red traffic light turned green. As the distance or transit time from emission to sampling increased, the size distribution shifted to a larger particle size, which confirmed the source assignments. To determine the distribution of emissions from individual vehicles, we correlated camera images with the spike contribution to particle number concentration at each time point. A small percentage of motor vehicles were found to emit a disproportionally large concentration of nanoparticles, and these high emitters included both spark-ignition (SI) and heavy-duty diesel (HDD) vehicles. In addition to characterizing the contribution of the spikes (local sources) to the ambient number concentration, we developed a method to determine the net contribution of motor vehicles (all sources) to the total mass concentration of ambient nanoparticles. To do this, we correlated the concentration of spikes with measurements of fast changes in the chemical composition of nanoparticles measured with the nano aerosol mass spectrometer (NAMS; built by the Johnston group). The NAMS irradiates individual, size-selected nanoparticles with a high-energy laser pulse to generate a mass spectrum consisting of multiply charged atomic ions. The elemental composition of each particle was determined from the ion signal intensities of each element. However, overlapping mass-to-charge ratios (m/z) at 4 m/z (O(+4) and C(+3)) and at 8 m/z (O(+2) and S(+4)) needed to be separated into their component ions to obtain a representative composition. To do this, we developed a method to deconvolute these ion signals using sucrose and ammonium sulfate [(NH4)2SO4] as calibration standards. With this approach, the differences between the expected and measured elemental mole fractions of carbon (C), oxygen (O), nitrogen (N), and sulfur (S) for a variety of test particles were generally much less than 10%. Ambient nanoparticles were found to consist mostly of C, O, N, and S. Many particles also contained silicon (Si). The elemental compositions were apportioned into molecular species that are commonly found in ambient aerosol: sulfate (SO4(2-)), nitrate (NO3-), ammonium (NH4+), carbonaceous matter, and when present, silicon dioxide (SiO2). Correlating NAMS chemical-composition measurements with spike contributions allowed for the development of a chemical profile representing motor vehicle emissions, which could be used to apportion their total contribution to the ambient nanoparticle mass. Particles originating from motor vehicles had compositions dominated by unoxidized carbonaceous matter, whereas non-motor vehicle particles consisted mostly of SO42-, NO3-, and oxidized carbonaceous matter. Motor vehicles were found to contribute up to 48% and 60% of the nanoparticle mass and number concentrations, respectively, in the winter measurement period, but only 16% and 49% of the nanoparticle mass and number concentrations, respectively, in the summer period. Chemical-composition profiles and contributions of SI versus HDD vehicles to the nanoparticle mass concentration were estimated by correlating still camera images, chemical composition, and spike contributions at each time point. The total mass contributions from SI and HDD vehicles were roughly equal, but the uncertainty in the split was large. The results of this study suggest that nanoparticle concentrations will be higher adjacent to an intersection than along the same roadway but further from an intersection. Possible ways to reduce the motor vehicle contribution to ambient nanoparticulate matter include minimizing stop-and-go activity at an intersection (i.e., vehicles accelerating after a red light turns green) and identifying the small fraction of motor vehicles that emit a disproportionally large number of nanoparticles.

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