Ambient air metallic elements (Mn, Fe, Zn, Cr, Cu, and Pb) pollutants sources study at a rural resident area near Taichung Thermal Power Plant and Industrial Park: 6-month observations
详细信息    查看全文
  • 作者:Guor-Cheng Fang ; Yuan-Jie Zhuang ; Yu-Chen Kuo…
  • 关键词:Total suspended particulate ; Dry deposition plate ; PCA ; Metallic element ; HYSPLIT
  • 刊名:Environmental Earth Sciences
  • 出版年:2016
  • 出版时间:April 2016
  • 年:2016
  • 卷:75
  • 期:7
  • 全文大小:1,489 KB
  • 参考文献:Agency for Toxic Substances and Disease Registry (ATSDR) (2004) Public health statement copper. Department of Health and Human Services. Public Health Service Agency for Toxic Substances and Disease Registry. CAS#: 7440-50-8r>Amato F, Pandolfi M, Moreno T, Furger M, Pey J, Alastuey A, Bukowiecki N, Prevot ASH, Baltensperger U, Querol X (2011a) Sources and variability of inhalable road dust particles in three European cities. Atmos Environ 45(37):6777–6787CrossRef r>Amato F, Viana M, Richard A, Furger M, Prévôt ASH, Nava S, Lucarelli F, Bukowiecki N, Alastuey A, Reche C, Moreno T, Pandolfi M, Pey J, Querol X (2011b) Size and time-resolved roadside enrichment of atmospheric particulate pollutants. Atmos Chem Phys 11(6):2917–2931CrossRef r>Buseck PR, Adachi K (2008) Nanoparticles in the atmosphere. Elements. 4:389–394CrossRef r>Choi EM, Kim SH, Holsen TM, Yi SM (2009) Total gaseous concentrations in mercury in Seoul, Korea: local sources compared to long-range transport from China and Japan. Environ Pollut 157(3):816–822CrossRef r>Connan O, Maro D, Hebert D, Roupsard P, Goujon R, Letellier B, LeCavelier S (2013) Wet and dry deposition of particles associated metals (Cd, Pb, Zn, Ni, Hg) in a reral wetland wite, Marais Vernier, France. Atmos Environ 67:394–403CrossRef r>Draxler RR (1999) HYSPLIT4 user's guide. NOAA Tech. Memo. ERL ARL-230, NOAA Air Resources Laboratory, Silver Spring, MDr>Fabretti JF, Sauret N, Gal JF, Maria PC, Schärer U (2009) Elemental characterization and source identification of PM2.5 using positive matrix factorization: the Malraux road tunnel, Nice, France. Atmos Res 94(2):320–329CrossRef r>Fang GC, Zheng YC (2014) Diurnal ambient air particles, metallic elements dry deposition, concentrations study during year of 20122013 at a traffic site. Effect of typhoon on atmospheric particulates in autumn in central Taiwan. Atmos Environ 88:39–46CrossRef r>Fang GC, Lin S Jay, Chang SY, Chou CCK (2009a) Effect of typhoon on atmospheric particulates in autumn in central Taiwan. Atmos Environ 43(38):6039–6048CrossRef r>Fang GC, Basu N, Nam DH, Yang IL (2009b) Characterization of ambient air particulates and particulate mercury at Sha-Lu, Central Taiwan. Environ Forensics 10(4):277–285CrossRef r>Fang GC, Chiang HC, Chen YC, Xiao YF, Zhuang YJ (2014) Particulates and metallic elements monitoring at two sampling sites (Harbor, Airport) in Taiwan. Environ Forensics. 15:296–305CrossRef r>Funasaka K, Sakai M, Shinya M, Miyazaki T, Kamiura T, Kaneco S, Ohta K, Fujita T (2003) Size distributions and characteristics of atmospheric inorganic particles by regional comparative study in Urban Osaka, Japan. Atmos Environ 37:4597–4605CrossRef r>Gietl JK, Lawrence R, Thorpe AJ, Harrison RM (2010) Identification of brake wear particles and derivation of a quantitative tracer for brake dust at a major road. Atmos Environ 44(2):141–146CrossRef r>Ho KF, Lee SC, Chiu GMY (2002) Characterization of selected volatile organic compounds, polycyclic aromatic hydrocarbons and carbonyl compounds at a roadside monitoring station. Atmos Environ 36(1):57–65CrossRef r>Horvath H, Kasaharat M, Pesava P (1996) The size distribution and composition of the atmospheric aerosol at a rural and nearby urban location. J Aerosol Sci 24:417–435CrossRef r>Hu Y, Lin J, Zhang S, Kong L, Fu H, Chen Jianmin (2015) Identification of the typical metal particles among haze, fog, and clear episodes in the Beijing atmosphere. Sci Total Environ 551(1):369–380CrossRef r>Jackson MM, Noll KE, Holsen TM (1998) Dry deposition model for atmospheric particles. J Aerosol Sci 20(2):1229–1230CrossRef r>Jahn HJ, Schneider A, Breitner S, Eissner R, Wendisch M, Kramer A (2011) Particulate matter pollution in the megacities of the Pearl River Delta, China—a systematic literature review and health risk assessment. Int J Hyg Environ Health 214(4):281–295r>Lee S, Liu W, Wang Y, Russell AG, Edgerton ES (2008) Source apportionment of PM2.5: comparing PMF and CMB results for four ambient monitoring sites in the southeastern United States. Atmos Environ 42:4126–4137CrossRef r>Lee PK, Choi BY, Kang MJ (2015) Assessment of mobility and bio-availability of heavy metals in dry depositions of Asian dust and implications for environmental risk. Chemosphere 119:1411–1421CrossRef r>Mbengue S, Alleman LY, Flament P (2014) Size-distributed metallic elements in submicronic and ultrafine atmospheric particles from urban and industrial areas in northern France. Atmos Res 135–136:35–47CrossRef r>Pakkanen TA, Kerminen VM, Korhonen CH, Hillamo RE, Aarnio PA, Koskentalo T, Maenhaut W (2001) Urban and rural ultrafine (PM0.1) particles in the Helsinki area. Atmos Environ 35:4593–4607CrossRef r>Pey J, Querol X, Alastuey A (2010) Discriminating the regional and urban contributions in the North-Western Mediterranean: PM levels and composition. Atmos Environ 44(13):1587–1596CrossRef r>Rajab JM, MatJafri MZ, Lim HS (2013) Combining multiple regression and principal component analysis for accurate predictions for column ozone in Peninsular Malaysia. Atmos Environ 71:36–43CrossRef r>Rolph GD, Ngan F, Draxler RR (2014) Modeling the fallout from stabilized nuclear clouds using the HYSPLIT atmospheric dispersion model. J Environ Radioact 136:41–55CrossRef r>Stanek LW, Sacks JD, Dutton SJ, Dubois LB (2011) Attributing health effects to apportioned components and sources of particulate matter: an evaluation of collective results. Atmos Environ 45:5655–5663CrossRef r>Tecer LH, Tuncel G, Karaca F, Alagha O, Süren P, Zararsız A, Kırmaz R (2012) Metallic composition and source apportionment of fine and coarse particles using positive matrix factorization in the southern Black Sea atmosphere. Atmos Res 118(15):153–169CrossRef r>Terry BC, Duckenfield KU, Landa ER, Callender E (2004) Tire-wear particles as a source of zinc to the environment. Environ Sci Technol 38:4206–4214CrossRef r>United States Environmental Protection Agency (EPA) (2015) Manganese compounds. Technology transfer network—air toxics website. http://​www.​epa.​gov/​airtoxics/​hlthef/​manganes.​html . Accessed 25 April 2015r>Wang Y, Stein AF, Draxler RR, Rosa JD, Zhang X (2011) Global sand and dust storms in 2008: observation and HYSPLIT model verification. Atmos Environ 45(35):6368–6381CrossRef r>Wang L, Wang S, Zhang L, Wang Y, Zhang Y, Nielsen C, McElroy MB, Hao J (2014) Source apportionment of atmospheric mercury pollution in China using the GEOS-Chem model. Environ Pollut 190:166–175CrossRef r>
  • 作者单位:Guor-Cheng Fang (1) r> Yuan-Jie Zhuang (2) r> Yu-Chen Kuo (2) r> Meng-Hsien Cho (2) r>r>1. Department of Safety, Health, and Environmental Engineering, Hungkuang University, Sha-Lu, Taichung, 433, Taiwan, ROC r> 2. Department of Biotechnology, National Formosa University, Yunlin, 63208, Taiwan, ROC r>
  • 刊物类别:Earth and Environmental Science
  • 刊物主题:None Assigned
  • 出版者:Springer Berlin Heidelberg
  • ISSN:1866-6299
文摘
The Longjing area is located at the Taichung, in central Taiwan. And it also near the Taichung Thermal Power Plant (TTPP) and Taichung Harbor Kwan-Lien Park (THKLP). Thus, this study measured the ambient air particulates and metallic elements concentrations using total suspended particulates (TSP) at Long Cyuan Elementary School (LCYES), Lung Ching Elementary School (LCHES), and Long Shan Primary School (LSPS) sampling sites at Longjing area. Because of the unique characteristic locations, therefore, this study focused on monitor ambient air particles and metallic element [Hg(p) Mn, Fe, Zn, Cr, Cu, and Pb] concentrations, particles and metallic element dry deposition around the Longjing area. In addition, method of back trajectory analysis was used to find the pollutants parcels in this study. Moreover, Principal Component Analysis (PCA) method was also applied in the identifying the possible sources of the ambient air pollutants at Longjing area. The results indicated that the LCYES has the lowest pollutants concentrations when compared with LCHES and LSPS sampling sites. The major pollutants sources were come from China especially in January. These pollutants will come to Taiwan along with dust storm accompaning exhausted gas from TTPP and THKLP. And the highest particulates bound mercury were in January. Moreover, PCA results also show that the factor loading values >0.7 frequency for metallic elements Mn, Fe, Zn and Hg(p) were greater than the other metallic elements. Thus, we concluded that the major pollutants were mainly from vehicles emissions, transport emissions and steel factory at THKLP and TTPP sampling site. Potential significant health impacts and concern at the Longjing sampling site are needed for this study.

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700