NO to NO2 conversion rate analysis, and implications for dispersion model chemistry methods using Las Vegas, Nevada near-road field measurements

被引:49
作者
Kimbrough, Sue [1 ]
Owen, R. Chris [2 ]
Snyder, Michelle [3 ]
Richmond-Bryant, Jennifer [4 ]
机构
[1] US EPA, Off Res & Dev, Natl Risk Management Res Lab, 109 TW Alexander Dr, Res Triangle Pk, NC 27711 USA
[2] US EPA, Off Air Qual Planning & Stand, 109 TW Alexander Dr, Res Triangle Pk, NC 27711 USA
[3] Univ N Carolina, Inst Environm, Ctr Environm Modeling Policy Dev, 100 Europa Dr, Chapel Hill, NC 27517 USA
[4] US EPA, Off Res & Dev, Natl Ctr Environm Assessment, 109 TW Alexander Dr, Res Triangle Pk, NC 27711 USA
关键词
NO; NO2; NOx; Near-source; Air pollution; Motor vehicle emissions; AIR-POLLUTION; NITROGEN-DIOXIDE; EMISSIONS; RATIOS;
D O I
10.1016/j.atmosenv.2017.06.027
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The nitrogen dioxide/oxides of nitrogen (NO2/NOX) ratio is an important surrogate for NO to NO2 chemistry in dispersion models when estimating NOX impacts in a near-road environment. Existing dispersion models use different techniques and assumptions to represent NO to NO2 conversion and do not fully characterize all of the important atmospheric chemical and mechanical processes. Thus, "real-world" ambient measurements must be analyzed to assess the behavior of NO2/NOX ratios near road-ways. An examination of NO2/NOX ratio data from a field study conducted in Las Vegas, Nevada (NV), from mid-December, 2008 through mid-December, 2009 provides insights into the appropriateness of assumptions about the NO2/NOx ratio included in dispersion models. Data analysis indicates multiple factors affect the downwind NO2/NOX ratio. These include spatial gradient, background ozone (O-3), source emissions of NO and NO2, and background NO2/NOX ratio. Analysis of the NO2/NOX ratio spatial gradient indicates that under high O-3 conditions, the change in the ratio is fairly constant once a certain O-3 threshold (>= 30 ppb) is reached. However, under low O-3 conditions (<30 ppb), there are differences between weekdays and weekends, most likely due to a decline in O-3 concentrations during the weekday morning hours, reducing the O-3 available to titrate the emitted NO, allowing lower NO2/NOX ratios. These results suggest that under high O-3 conditions, NOX chemistry is driving the NO2/NOX ratios whereas under low O-3 conditions, atmospheric mixing is the driving factor. Published by Elsevier Ltd.
引用
收藏
页码:23 / 34
页数:12
相关论文
共 51 条
[1]   Evidence of increased mass fraction of NO2 within real-world NOx emissions of modern light vehicles -: derived from a reliable online measuring method [J].
Alvarez, Robert ;
Weilenmann, Martin ;
Favez, Jean-Yves .
ATMOSPHERIC ENVIRONMENT, 2008, 42 (19) :4699-4707
[2]  
[Anonymous], EPA454R12001
[3]  
[Anonymous], 2016, Air Pollutant Emissions Trends Data
[4]  
[Anonymous], 1984, CALINE4 A DISPERSION
[5]   Atmospheric chemistry of VOCs and NOx [J].
Atkinson, R .
ATMOSPHERIC ENVIRONMENT, 2000, 34 (12-14) :2063-2101
[6]   IMPROVEMENT OF THE MODELING OF DAYTIME NITROGEN-OXIDE OXIDATION IN PLUMES BY USING INSTANTANEOUS PLUME DISPERSION PARAMETERS [J].
BANGE, P ;
JANSSEN, LHJM ;
NIEUWSTADT, FTM ;
VISSER, H ;
ERBRINK, JJ .
ATMOSPHERIC ENVIRONMENT PART A-GENERAL TOPICS, 1991, 25 (10) :2321-2328
[7]   Correlation of nitrogen dioxide with other traffic pollutants near a major expressway [J].
Beckerman, Bernardo ;
Jerrett, Michael ;
Brook, Jeffrey R. ;
Verma, Dave K. ;
Arain, Muhammad A. ;
Finkelstein, Murray M. .
ATMOSPHERIC ENVIRONMENT, 2008, 42 (02) :275-290
[8]  
Berkowicz R., 2011, NO2 CHEM SCHEME OSPM
[9]   Estimations of road vehicle primary NO2 exhaust emission fractions using monitoring data in London [J].
Carslaw, DC ;
Beevers, SD .
ATMOSPHERIC ENVIRONMENT, 2005, 39 (01) :167-177
[10]   Evidence of an increasing NO2/NOX emissions ratio from road traffic emissions [J].
Carslaw, DC .
ATMOSPHERIC ENVIRONMENT, 2005, 39 (26) :4793-4802