Chemical speciation of size-segregated floor dusts and airborne magnetic particles collected at underground subway stations in Seoul, Korea.

Previous studies have reported the major chemical species of underground subway particles to be Fe-containing species that are generated from wear and friction processes at rail-wheel-brake and catenaries-pantographs interfaces. To examine chemical composition of Fe-containing particles in more details, floor dusts were collected at five sampling locations of an underground subway station. Size-segregated floor dusts were separated into magnetic and non-magnetic fractions using a permanent magnet. Using X-ray diffraction (XRD) and scanning electron microscopy/energy dispersive X-ray spectrometry (SEM/EDX), iron metal, which is relatively harmless, was found to be the dominating chemical species in the floor dusts of the <25 μm size fractions with minor fractions of Mg, Al, Si, Ca, S, and C. From SEM analysis, the floor dusts of the <25 μm size fractions collected on railroad ties appeared to be smaller than 10 μm, indicating that their characteristics should somewhat reflect the characteristics of airborne particles in the tunnel and the platform. As most floor dusts are magnetic, PM levels at underground subway stations can be controlled by removing magnetic indoor particles using magnets. In addition, airborne subway particles, most of which were smaller than 10 μm, were collected using permanent magnets at two underground subway stations, namely Jegi and Yangjae stations, in Seoul, Korea. XRD and SEM/EDX analyses showed that most of the magnetic aerosol particles collected at Jegi station was iron metal, whereas those at Yangjae station contained a small amount of Fe mixed with Na, Mg, Al, Si, S, Ca, and C. The difference in composition of the Fe-containing particles between the two subway stations was attributed to the different ballast tracks used.

[1]  Per Gustavsson,et al.  Incidence of lung cancer among subway drivers in Stockholm. , 2008, American journal of industrial medicine.

[2]  Dong-Uk Park,et al.  Characteristics of PM10, PM2.5, CO2 and CO monitored in interiors and platforms of subway train in Seoul, Korea. , 2008, Environment international.

[3]  Sophie Lanone,et al.  Biological effects of particles from the paris subway system. , 2007, Chemical research in toxicology.

[4]  Lennart Möller,et al.  Subway particles are more genotoxic than street particles and induce oxidative stress in cultured human lung cells. , 2005, Chemical research in toxicology.

[5]  E. Petrovský,et al.  Magnetic properties of magnetite prepared by ball-milling of hematite with iron , 2000 .

[6]  J. Osán,et al.  A Monte Carlo program for quantitative electron-induced X-ray analysis of individual particles. , 2003, Analytical chemistry.

[7]  Sonja N Sax,et al.  Elevated airborne exposures of teenagers to manganese, chromium, and iron from steel dust and New York City's subway system. , 2004, Environmental science & technology.

[8]  E. Appel,et al.  Magnetic properties of road dust from Visakhapatnam (India)––relationship to industrial pollution and road traffic , 2004 .

[9]  Abdel Hameed A. Awad,et al.  Environmental Study in Subway Metro Stations in Cairo, Egypt , 2002 .

[10]  Meehye Lee,et al.  Role of Chinese wind-blown dust in enhancing environmental pollution in Metropolitan Seoul. , 2008, Environmental pollution.

[11]  Koen Janssens,et al.  Analysis of X‐ray spectra by iterative least squares (AXIL): New developments , 1994 .

[12]  C. Sudakar,et al.  Synthesis of acicular hydrogoethite (α-FeOOH·xH2O; 0.1 < x < 0.22) particles using morphology controlling cationic additives and magnetic properties of maghemite derived from hydrogoethite , 2002 .

[13]  Shila Maskey,et al.  Source identification of particulate matter collected at underground subway stations in Seoul, Korea using quantitative single-particle analysis , 2010 .

[14]  J. Osán,et al.  Chemical speciation of individual atmospheric particles using low-Z electron probe X-ray microanalysis characterizing "Asian Dust" deposited with rainwater in Seoul, Korea , 2001 .

[15]  A Seaton,et al.  The London Underground: dust and hazards to health , 2005, Occupational and Environmental Medicine.

[16]  C. Ro,et al.  An expert system for chemical speciation of individual particles using low-Z particle electron probe X-ray microanalysis data. , 2004, Analytical chemistry.

[17]  Martin Braniš,et al.  The contribution of ambient sources to particulate pollution in spaces and trains of the Prague underground transport system , 2006 .

[18]  Zoltán Homonnay,et al.  Properties and sources of individual particles and some chemical species in the aerosol of a metropolitan underground railway station , 2009 .

[19]  Christer Johansson,et al.  Particulate matter in the underground of Stockholm , 2002 .

[20]  Yoichi Araki,et al.  SEASONAL VARIATION AND THEIR CHARACTERIZATION OF SUSPENDED PARTICULATE MATTER IN THE AIR OF SUBWAY STATIONS , 2001 .

[21]  H. Karlsson,et al.  Comparison of genotoxic and inflammatory effects of particles generated by wood combustion, a road simulator and collected from street and subway. , 2006, Toxicology letters.

[22]  Timo Mäkelä,et al.  The concentrations and composition of and exposure to fine particles (PM2.5) in the Helsinki subway system , 2005 .

[23]  L. Murruni,et al.  Concentrations and elemental composition of particulate matter in the Buenos Aires underground system , 2009 .

[24]  Yang Yu,et al.  Magnetic and geochemical characterization of iron pollution in subway dusts in Shanghai, China , 2011 .

[25]  Erwin Appel,et al.  Magnetic susceptibility mapping of roadside pollution , 1999 .

[26]  Patrick Chazette,et al.  Link between aerosol optical, microphysical and chemical measurements in an underground railway station in Paris , 2009 .

[27]  Young Chul Song,et al.  Characterization of Summertime Aerosol Particles Collected at Subway Stations in Seoul, Korea Using Low-Z Particle Electron Probe X-ray Microanalysis , 2010 .

[28]  H. Stanjek,et al.  Micro-scale grain-size analysis and magnetic properties of coal-fired power plant fly ash and its relevance for environmental magnetic pollution studies , 2008 .

[29]  Chul-Un Ro,et al.  Chemical compositions of subway particles in Seoul, Korea determined by a quantitative single particle analysis. , 2008, Environmental science & technology.

[30]  R. Colvile,et al.  Levels of particulate air pollution, its elemental composition, determinants and health effects in metro systems , 2007 .

[31]  J. Osán,et al.  Determination of Chemical Species in Individual Aerosol Particles Using Ultrathin Window EPMA , 2000 .

[32]  Chi Nyon Kim,et al.  Spatial distribution of particulate matter (PM10 and PM2.5) in Seoul Metropolitan Subway stations. , 2008, Journal of hazardous materials.

[33]  Ernest Weingartner,et al.  Iron, manganese and copper emitted by cargo and passenger trains in Zürich (Switzerland): Size-segregated mass concentrations in ambient air , 2007 .

[34]  Ian D. Williams,et al.  Characterisation of airborne particles in London by computer-controlled scanning electron microscopy , 1999 .

[35]  J. Osán,et al.  Determination of low-Z elements in individual environmental particles using windowless EPMA. , 1999, Analytical chemistry.

[36]  U. de Faire,et al.  Blood markers of inflammation and coagulation and exposure to airborne particles in employees in the Stockholm underground , 2008, Occupational and Environmental Medicine.

[37]  Å. Holgersson,et al.  Mechanisms related to the genotoxicity of particles in the subway and from other sources. , 2008, Chemical research in toxicology.