Johnston Murray V, Klems Joseph P, Zordan Christopher A, Pennington M Ross, Smith James N
Department of Chemistry and Biochemistry, University of Delaware, Newark, 19716, USA.
Res Rep Health Eff Inst. 2013 Feb(173):3-45.
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.
大量研究表明,暴露于机动车尾气排放中会增加高危人群心脏病发作、哮喘发作以及就医的概率。然而,尽管许多研究聚焦于高速公路附近环境纳米颗粒的测量,但并未关注特定的道路区域,如人口密集中心附近的十字路口。在这些地点,已观察到颗粒物数量浓度出现非常强烈的峰值。这些峰值与机动车活动有关,并且有可能大幅增加暴露量。确定这些峰值的贡献和组成对于建立暴露模型和减排策略至关重要。为了确定颗粒物峰值对环境数量浓度的贡献,我们实施了基于小波的算法,从2009年夏季和冬季在特拉华州威尔明顿一个道路交叉口附近进行的测量中分离出颗粒物峰值,该交叉口每天约有28000辆车通过。这些测量包括由冷凝粒子计数器(CPC*;TSI公司,明尼苏达州圣保罗)和快速移动粒子粒度分析仪(FMPS)每秒记录一次的数量浓度和粒径分布。信号的高频部分由一系列数量浓度的突然峰值组成,长度从几秒到几十秒不等,占每日环境数量浓度的3%至35%,有时峰值贡献超过每小时数量浓度的50%。当数据按颗粒体积加权时,该信号部分对空气动力学直径小于或等于0.1微米的颗粒物(PM0.1)的每日浓度平均贡献10%至20%。观察颗粒物浓度峰值的首选位置是测量点周围那些机动车在红灯变绿后加速的区域。随着从排放到采样的距离或传输时间增加,粒径分布向更大粒径转移,这证实了源的归属。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颗粒物数量浓度的峰值贡献相关联。发现一小部分机动车排放的纳米颗粒浓度不成比例地高,这些高排放源包括火花点火(SI)车辆和重型柴油(HDD)车辆。除了确定峰值(局部源)对环境数量浓度的贡献外,我们还开发了一种方法来确定机动车(所有源)对环境纳米颗粒总质量浓度的净贡献。为此我们将峰值浓度与用纳米气溶胶质谱仪(NAMS;由约翰斯顿小组制造)测量的纳米颗粒化学成分快速变化的测量结果相关联。NAMS用高能激光脉冲照射单个、按尺寸选择的纳米颗粒,以产生由多电荷原子离子组成的质谱。每个颗粒的元素组成由每种元素的离子信号强度确定。然而,4 m/z(O(+4)和C(+3))以及8 m/z(O(+2)和S(+))处重叠的质荷比(m/z)需要分离成其组成离子以获得代表性组成。为此,我们开发了一种使用蔗糖和硫酸铵[(NH4)2SO4]作为校准标准对这些离子信号进行去卷积的方法。通过这种方法,对于各种测试颗粒,碳(C)氧(O)氮(N)和硫(S)的预期和测量元素摩尔分数之间的差异通常远小于10%。发现环境纳米颗粒主要由C、O、N和S组成。许多颗粒还含有硅(Si)。元素组成被分配到环境气溶胶中常见的分子物种:硫酸盐(SO4(2-))、硝酸盐(NO3-)、铵(NH4+)、碳质物质,以及(如果存在)二氧化硅(SiO2)。将NAMS化学成分测量结果与峰值贡献相关联,有助于建立代表机动车排放的化学特征,可用于确定其对环境纳米颗粒质量的总贡献。源自机动车的颗粒组成以未氧化的碳质物质为主,而非机动车颗粒主要由SO42-、NO3-和氧化的碳质物质组成。发现在冬季测量期间,机动车对纳米颗粒质量和数量浓度的贡献分别高达48%和60%,但在夏季期间分别仅为16%和49%。通过将静态相机图像、化学成分和每个时间点的峰值贡献相关联,估计了SI车辆和HDD车辆对纳米颗粒质量浓度的化学特征和贡献。SI车辆和HDD车辆的总质量贡献大致相等,但两者比例的不确定性很大。本研究结果表明,十字路口附近的纳米颗粒浓度将高于同一条道路但离十字路口更远的地方。减少机动车对环境纳米颗粒物贡献的可能方法包括尽量减少十字路口的启停活动(即红灯变绿后车辆加速)以及识别排放不成比例大量纳米颗粒的一小部分机动车。