Measurement of ambient PAHs in Kumamoto: Differentiating local and transboundary air pollution

ABSTRACTWe developed an index to investigate the effect of transboundary air pollution (TAP) on the air quality of Kumamoto City, Japan. We estimated the effect of TAP by using the index and positive matrix factorization (PMF). Polycyclic aromatic hydrocarbons (PAHs) and trace metals were analyzed from the daily samples of the Total Suspended Particles (TSPs) collected seasonally from Oct. 2014 to Aug. 2015. These chemical components exhibited high concentrations in spring and winter, which is consistent with the data in the literature. Pb was identified as the TAP tracer owing to its high concentrations in winter and spring. Indeno(1, 2, 3-cd)pyrene (IcdP) was used as the local emission tracer in Kumamoto on the basis of previous studies. We applied the IcdP/Pb ratio as the index. The index enables the detection of TAP in daily data sets. PMF identified six factors: soil and road dust, biomass and waste burning, heavy oil combustion, fishing boats, vehicle emission, and coal combustion. The average contribution of TAP on the days when transboundary pollution was high was evaluated as being 46%.

[1]  Ranjeet S. Sokhi,et al.  Atmospheric polycyclic aromatic hydrocarbons: Source attribution, emission factors and regulation , 2008 .

[2]  Y. J. Kim,et al.  Source apportionment of fine carbonaceous particles by positive matrix factorization at Gosan background site in East Asia. , 2008, Environment international.

[3]  Miguel Luesma Castán,et al.  PAH in airborne particulate matter. Carcinogenic character of PM10 samples and assessment of the energy generation impact , 2011 .

[4]  Greet Janssens-Maenhout,et al.  Emissions of air pollutants and greenhouse gases over Asian regions during 2000–2008: Regional Emission inventory in ASia (REAS) version 2 , 2013 .

[5]  C. Chan,et al.  Transboundary and Local Air Pollutants in Western Japan Distinguished on the Basis of Ratios of Metallic Elements in Size-Segregated Aerosols , 2017 .

[6]  H. Ueda,et al.  Emission and atmospheric transport of particulate PAHs in Northeast Asia. , 2012, Environmental science & technology.

[7]  PMF analysis of impacts of SO2 from Miyakejima and Asian Continent on precipitation sulfate in Japan , 2010 .

[8]  Hajime Okamoto,et al.  Global three‐dimensional simulation of aerosol optical thickness distribution of various origins , 2000 .

[9]  P. Paatero,et al.  Positive matrix factorization: A non-negative factor model with optimal utilization of error estimates of data values† , 1994 .

[10]  Roy M Harrison,et al.  Estimation of the contributions of brake dust, tire wear, and resuspension to nonexhaust traffic particles derived from atmospheric measurements. , 2012, Environmental science & technology.

[11]  S. Dullinger,et al.  Pilot study on road traffic emissions (PAHs, heavy metals) measured by using mosses in a tunnel experiment in Vienna, Austria , 2006, Environmental science and pollution research international.

[12]  John Kennedy Mwangi,et al.  An Overview: Polycyclic Aromatic Hydrocarbon Emissions from the Stationary and Mobile Sources and in the Ambient Air , 2015 .

[13]  E. Fridell,et al.  Characterisation of particulate matter and gaseous emissions from a large ship diesel engine , 2009 .

[14]  C. Venkataraman,et al.  Positive matrix factorization and trajectory modelling for source identification: A new look at Indian Ocean Experiment ship observations , 2008 .

[15]  A. Fushimi,et al.  Mode and Place of Origin of Carbonaceous Aerosols Transported From East Asia to Cape Hedo, Okinawa, Japan , 2015 .

[16]  Roy M. Harrison,et al.  Identification of brake wear particles and derivation of a quantitative tracer for brake dust at a major road , 2010 .

[17]  T. Ramdahl Retene—a molecular marker of wood combustion in ambient air , 1983, Nature.

[18]  B. Holben,et al.  Single-Scattering Albedo and Radiative Forcing of Various Aerosol Species with a Global Three-Dimensional Model , 2002 .

[19]  X. Querol,et al.  Size-segregated chemical composition of aerosol emissions in an urban road tunnel in Portugal , 2013 .

[20]  Sangi Lee,et al.  Characterization of PM2.5-bound polycyclic aromatic hydrocarbons in Atlanta , 2009 .

[21]  Chin-Yu Hsu,et al.  Characteristics, Sources, and Health Risks of Atmospheric PM2.5-Bound Polycyclic Aromatic Hydrocarbons in Hsinchu, Taiwan , 2017 .

[22]  K. Hayakawa,et al.  Polycyclic aromatic hydrocarbons and nitropolycyclic aromatic hydrocarbons in urban air particulates and their relationship to emission sources in the Pan–Japan Sea countries , 2005 .

[23]  Wen-Jhy Lee,et al.  Impact of using fishing boat fuel with high poly aromatic content on the emission of polycyclic aromatic hydrocarbons from the diesel engine , 2006 .

[24]  Kei Sato,et al.  Long-range transport of particulate polycyclic aromatic hydrocarbons at Cape Hedo remote island site in the East China Sea between 2005 and 2008 , 2008 .

[25]  S. Emori,et al.  Simulation of climate response to aerosol direct and indirect effects with aerosol transport‐radiation model , 2005 .

[26]  X. Querol,et al.  Daily and hourly chemical impact of springtime transboundary aerosols on Japanese air quality , 2012 .

[27]  Jiamo Fu,et al.  Atmospheric levels and cytotoxicity of PAHs and heavy metals in TSP and PM2.5 at an electronic waste recycling site in southeast China , 2006 .

[28]  Xin Yang,et al.  Size distributions of polycyclic aromatic hydrocarbons in urban atmosphere: sorption mechanism and source contributions to respiratory deposition , 2015 .

[29]  Dongsheng Chen,et al.  Trends of PM2.5 and Chemical Composition in Beijing, 2000-2015 , 2017 .

[30]  A. Mastral,et al.  Nature and sources of particle associated polycyclic aromatic hydrocarbons (PAH) in the atmospheric environment of an urban area. , 2013, Environmental pollution.

[31]  Xiaole Pan,et al.  Sensitivity analysis of source regions to PM2.5 concentration at Fukue Island, Japan , 2014, Journal of the Air & Waste Management Association.

[32]  Yuanan Lu,et al.  Analysis of the Effect of Meteorological Factors on PM2.5-Associated PAHs during Autumn-Winter in Urban Nanchang , 2017 .

[33]  K. Hayakawa Environmental Behaviors and Toxicities of Polycyclic Aromatic Hydrocarbons and Nitropolycyclic Aromatic Hydrocarbons , 2016 .

[34]  Thomas W. Kirchstetter,et al.  On-Road Emissions of Particulate Polycyclic Aromatic Hydrocarbons and Black Carbon from Gasoline and Diesel Vehicles , 1998 .

[35]  A. Piazzalunga,et al.  High secondary aerosol contribution to particulate pollution during haze events in China , 2014, Nature.

[36]  M. Hayashi,et al.  Transported and Local Organic Aerosols over Fukuoka, Japan , 2013 .

[37]  A. Mellouki,et al.  Chemical characteristics and influence of continental outflow on PM1.0, PM2.5 and PM10 measured at Tuoji island in the Bohai Sea. , 2016, The Science of the total environment.

[38]  Yi-Fan Li,et al.  Seasonal variations of sources of polycyclic aromatic hydrocarbons (PAHs) to a northeastern urban city, China. , 2010, Chemosphere.

[39]  Yuanxun Zhang,et al.  Size Distribution and Sources of Trace Metals in Ultrafine/Fine/Coarse Airborne Particles in the Atmosphere of Shanghai , 2011 .

[40]  H. Takada,et al.  Seasonal variations of sulfate, carbonaceous species (black carbon and polycyclic aromatic hydrocarbons), and trace elements in fine atmospheric aerosols collected at subtropical islands in the East China Sea , 2004 .