Meteorology and photochemical air pollution in Southern Europe: Experimental results from EC research projects

被引:164
作者
Millan, M [1 ]
Salvador, R [1 ]
Mantilla, E [1 ]
Artinano, B [1 ]
机构
[1] CIEMAT,E-28040 MADRID,SPAIN
关键词
Mediterranean; air pollution; observations; mesoscale meteorology;
D O I
10.1016/1352-2310(95)00220-0
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The MECAPIP project of EC has served to document the summer atmospheric circulations and the related air pollution dynamics over Spain and the Western Mediterranean. The first includes surface wind convergence over the Iberian peninsula, large-scale compensatory subsidence over the surrounding coastal areas, and the formation of re-circulatory cells as a result of the sea breezes combining with up-slope winds and their return and compensatory flows. With respect to the second, experimental evidence indicates that, (a) during the day the sea breezes can transport ozone 60 to 100, or more, km inland, (b) during the afternoon, photo-oxidants are injected 3 to 5 km into the mid-troposphere over the Spanish Central plateau, and (c) stratified reservoir layers, stacked up to approximate to 2-3 km high, build up along the Mediterranean coast. These retain ozone from one day to the next and following days. The lowermost layers are drawn inland by the sea breeze during the day, and the aged pollutants can react with new coastal emissions. All of these processes have a marked diurnal cycle and can recur for many consecutive days or weeks. Tracer experiments show that the average return times for pollutants can be of the order of 2-3 d. This includes first emission on the coast in the morning, travel inland with sea breeze, convective and/or orographic injection in return flows followed by layering and subsidence over the sea, and their final re-entry with the sea breeze a few days later. All together, those mechanisms can be considered to form a large ''photochemical reactor'' which operates almost every day from spring to fall. It can generate ozone levels 2 to 3 times higher than EC directives for damages to vegetation 65 mu g m(-3) (approximate to 32 ppbv), 24 h avg. This work presents a summary of results illustrating some of the above-mentioned processes. Similar situations are also expected to occur in other Mediterranean regions. Copyright (C) 1996 Elsevier Science Ltd
引用
收藏
页码:1909 / 1924
页数:16
相关论文
共 19 条
[1]  
[Anonymous], P 4 EUR S PHYS CHEM
[2]  
Cantu V., 1977, RIV METEOROL AERONAU, VXXXVII, P265
[3]  
*COMM EUR COMM, 1988, 11590 EUR COMM EUR C
[4]  
*COMM EUR COMM, 1993, 15016 EUR COMM EUR C
[5]   DISTRIBUTION OF TROPOSPHERIC OZONE DETERMINED FROM SATELLITE DATA [J].
FISHMAN, J ;
WATSON, CE ;
LARSEN, JC ;
LOGAN, JA .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 1990, 95 (D4) :3599-3617
[6]   1ST EUROPEAN-COMMUNITY CAMPAIGN FOR REMOTE-SENSING OF ATMOSPHERIC POLLUTION, LACQ (FRANCE), 7-11 JULY 1975 [J].
GUILLOT, P ;
BONOMETTI, G ;
HASENJAEGER, H ;
VANDERMEULEN, A ;
HAMILTON, PM ;
HAULET, R ;
LAURENT, J ;
SANDRONI, S ;
CERUTTI, C ;
GIOVANELLI, G ;
TIRABASSI, T ;
VITTORI, O ;
PICCININI, P .
ATMOSPHERIC ENVIRONMENT, 1979, 13 (07) :895-917
[7]  
Guillot P., 1985, P 78 ANN M AIR POLL, P85
[8]  
HUA BL, 1983, J PHYS OCEANOGR, V13, P678, DOI 10.1175/1520-0485(1983)013<0678:ANSOTE>2.0.CO
[9]  
2
[10]   SEA-BREEZE CIRCULATION AND PHOTOCHEMICAL POLLUTION IN ATHENS, GREECE [J].
LALAS, DP ;
ASIMAKOPOULOS, DN ;
DELIGIORGI, DG ;
HELMIS, CG .
ATMOSPHERIC ENVIRONMENT, 1983, 17 (09) :1621-1632