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Transition metals in coarse, fine, very fine and ultra-fine particles from an interstate highway transect near Detroit

机译:来自底特律附近州际公路横断面的粗,细,非常细和超细颗粒中的过渡金属

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As one component of a study investigating the impact of vehicle emissions on near-road air quality, human exposures, and potential health effects, particles were measured from September 21 to October 30, 2010 on both sides of a major roadway (Interstate-96) in Detroit. Traffic moved freely on this 12 lane freeway with a mean velocity of 69 mi/hr. with little braking and acceleration. The UC Davis DELTA Group rotating drum (DRUM) impactors were used to collect particles in 8 size ranges at sites nominally 100 m south, 10 m north, 100 m north, and 300 m north of the highway. Ultra-fine particles were continuously collected at the 10 m north and 100 m north sites. Samples were analyzed every 3 h for mass (soft beta ray transmission), 42 elements (synchrotron-induced x-ray fluorescence) and optical attenuation (350 -800 nm spectroscopy). A three day period of steady southerly winds along the array allowed direct measurement of freeway emission rates for coarse (10 > D-p > 1.0 mu m), PM2.5, very fine (0.26 > D-p > 0.09 mu m), and ultra-fine (D-p < 0.09 mu m) particles. The PM2.5 mass concentrations were modeled using literature emission rates during the south to north wind periods, and averaged 1.6 +/- 0.5 mu g/m(3), versus the measured value of 2.0 +/- 0.7 mu g/m(3). Using European freeway emission rates from 2010, and modeling them at the I-96 site, we would predict roughly 3.1 mu g/m(3) of PM2.5 particles, corrected from the 4.9 PM10 value by their measured road dust contributions. Using California car and truck emission rates of 1973, this value would have been about 16 mu g/m(3), corrected down from the 19 mu g/m(3) PM5.0 using measured roadway dust contributions. This would have included 2.7 mu g/m(3) of lead, versus the 0.0033 mu g/m(3) measured. Very fine particles were distributed across the array with a relatively weak falloff versus distance. For the ultra-fine particles, emissions of soot and metals seen in vehicular braking studies correlated with traffic at the 10 m site, but only the soot was statistically significant at the 100 m north site. Otherwise, the 10 m north and 100 m north sites were essentially identical in mean concentration and highly correlated in time for most of the 5 week study. This result supports earlier publications showing the ability of very fine and ultra-fine particles to transport to sites well removed from the freeway sources. The concentrations of very fine and ultra-fine metals from brake wear and zinc in motor oil observed in Detroit have the potential of being a significant component in statistically established PM2.5 mortality rates. (C) 2016 The Authors. Published by Elsevier Ltd.
机译:作为研究车辆排放对近距离道路空气质量,人类暴露以及潜在健康影响的研究的一项内容,于2010年9月21日至10月30日在主要道路两侧进行了测量(96州际公路)在底特律。交通在这条12车道的高速公路上自由行驶,平均速度为69英里/小时。几乎没有制动和加速。加州大学戴维斯分校的DELTA Group旋转鼓(DRUM)冲击器用于在高速公路以南100 m,以北10 m,以北100 m和以北300 m的地点收集8个尺寸范围的颗粒。在北10 m和北100 m处连续收集超细颗粒。每3小时分析一次样品的质量(软β射线透射),42种元素(同步加速器诱导的X射线荧光)和光衰减(350 -800 nm光谱)。沿着阵列持续三天的稳定南风,可以直接测量高速公路的排放率,包括粗(10> Dp> 1.0微米),PM2.5,极细(0.26> Dp> 0.09微米)和超细(Dp <0.09微米)颗粒。 PM2.5的质量浓度是使用文献报道的南风到北风期间的浓度来模拟的,平均浓度为1.6 +/- 0.5μg / m(3),而测量值则为2.0 +/- 0.7μg / m( 3)。使用2010年以来的欧洲高速公路排放率,并在I-96站点进行建模,我们可以预测到PM2.5颗粒约为3.1μg / m(3),并通过测量的道路粉尘贡献从4.9 PM10值进行了校正。使用1973年加利福尼亚州的汽车和卡车排放速率,该值将约为16μg / m(3),使用测量的道路扬尘贡献值从19μg/ m(3)PM5.0向下修正。这将包括2.7μg / m(3)的铅,而测得的0.0033μg / m(3)。非常细的颗粒以相对较弱的衰减与距离分布在整个阵列中。对于超细颗粒,在车辆制动研究中看到的烟灰和金属的排放与10 m站点处的交通量相关,但只有烟灰在北100 m站点具有统计学意义。否则,在整个5周的研究中,北10 m和北100 m站点的平均浓度基本相同,并且时间上高度相关。该结果支持了较早的出版物,这些出版物显示了非常细的颗粒和超细的颗粒能够运输到从高速公路源完全移开的位置。在底特律观察到的来自刹车油和机油中锌的极细和超细金属的浓度可能是统计学确定的PM2.5死亡率的重要组成部分。 (C)2016作者。由Elsevier Ltd.发布

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