Spatial and temporal variations in airborne particulate matter (PM10 and PM2.5) across Spain 1999-2005

被引:284
作者
Querol, X. [1 ]
Alastuey, A. [1 ]
Moreno, T. [1 ]
Viana, M. M. [1 ]
Castillo, S. [1 ]
Pey, J. [1 ]
Rodriguez, S. [1 ]
Artinano, B. [2 ]
Salvador, P. [2 ]
Sanchez, M. [2 ]
Dos Santos, S. Garcia [3 ]
Garraleta, M. D. Herce [3 ]
Fernandez-Patier, R. [3 ]
Moreno-Grau, S. [4 ]
Negral, L. [4 ]
Minguillon, M. C. [1 ,5 ]
Monfort, E. [5 ]
Sanz, M. J. [6 ]
Palomo-Marin, R. [7 ]
Pinilla-Gil, E. [7 ]
Cuevas, E. [8 ]
de la Rosa, J. [9 ]
de la Campa, A. Sanchez [9 ]
机构
[1] CSIC, Inst Ciencias Tierra Jaume Almera, E-08028 Barcelona, Spain
[2] CIEMAT, E-28040 Madrid, Spain
[3] Inst Salud Carlos III, Madrid 28220, Spain
[4] Univ Pol Cartagena, Dept Ing Quim & Ambiental, Cartagena 30203, Spain
[5] Ins Tecnol Ceram, Castellon de La Plana 12006, Spain
[6] CEAM, Valencia 46998, Spain
[7] Univ Extremadura, Dept Quim Analit & Electroquim, E-06071 Badajoz, Spain
[8] INM, Observ Atmosfer Izana, Santa Cruz de Tenerife 38071, Spain
[9] Univ Huelva, Dept Geologia, Huelva, Spain
关键词
PM10; PM2.5; Spain; geochemistry; metals;
D O I
10.1016/j.atmosenv.2006.10.071
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Average ranges of particulate matter (PM10 and PM2.5) concentrations and chemical composition in Spain show significant variations across the country, with current PM10 levels at several industrial and traffic hotspots exceeding recommended pollution limits. Such variations and exceedances are linked to patterns of anthropogenic and natural PM emissions, climate, and reactivity/stability of particulate species. PM10 and PM2.5 concentrations reach 14-22 mu g PM10 m(-3) and 8-12 mu g PM2.5 m(-3) at most rural/regional background sites, 25-30 mu g PM 10 m(-3) and 15-20 mu g PM2.5 m(-3) at suburban sites, 30-46 mu g PM10 m(-3) and 20-30 mu g PM2.5 m(-3) at urban background and industrial sites, and 46-50 mu g PM10 m(-3) and 30-35 mu g PM2.5 m(-3) at heavy traffic hotpots. Spatial distributions show sulphate and carbon particle levels reach maxima in industrialised areas and large cities (where traffic emissions are higher), and nitrate levels increase from the Atlantic to the Mediterranean (independent of the regional NO, emissions). African dust outbreaks have an influence on the number of exceedances of the daily limit value, but its additional load on the mean annual PM10 levels is only highly significant in Southern Iberia and Canary and Balearic islands. The marine aerosol contribution is near one order of magnitude higher in the Canaries compared to the other regions. Important temporal influences include PM intrusion events from Africa (more abundant in February-March and spring-summer), regional-scale pollution episodes, and weekday versus weekend activity. Higher summer insolation enhances (NH4)(2)SO4 but depletes particulate NO3- (as a consequence of the thermal instability of ammonium nitrate in summer) and Cl- (due to HCl volatilisation resulting from the interaction of gaseous HNO3 with the marine NaCl), as well as generally increasing dry dust resuspension under a semi-arid climate. Average trace metal concentrations rise with the highest levels at industrial and traffic hotspots sites, in some cases (Ti, Cr, Mn, Cu, Zn, As, Sn, W, and Pb) exceeding rural background levels by over an order of magnitude. (C) 2006 Elsevier Ltd. All rights reserved.
引用
收藏
页码:3964 / 3979
页数:16
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