Reactions between ozone and building products: Impact on primary and secondary emissions

被引:93
作者
Nicolas, Melanie [1 ]
Ramalho, Olivier [1 ]
Maupetit, Francois [1 ]
机构
[1] CSTB, F-77447 Marne La Vallee 2, France
关键词
ozone; building products; secondary emissions; deposition velocity; indoor chemistry;
D O I
10.1016/j.atmosenv.2006.06.062
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Reactions of ozone on common building products were studied in a dedicated emission test chamber system. Fourteen new and unused products were exposed to 100-160 ppb of ozone at 23 degrees C and 50% RH during 48 h experiments. Ozone deposition velocities calculated at steady state were between 0.003 cm s(-1) (alkyd paint on polyester film) and 0. 108 cm s(-1) (pine wood board). All tested product showed modified emissions when exposed to ozone and secondary emissions of several aldehydes were identified. Carpets and wall coverings emitted mainly C-5-C-10 n-aldehydes, typical by-products of surface reactions. Linoleum, polystyrene tiles and pine wood boards also showed increased emissions of formaldehyde, benzaldehyde and hexanal associated with reduced emissions of unsaturated compounds suggesting the occurrence of gasphase reactions. The ozone removal on the different tested products was primarily associated with surface reactions. The relative contribution of gas-phase reactions to the total ozone removal was estimated to be between 5% and 30% for pine wood boards depending on relative humidity (RH) and on the incoming ozone concentration and 2% for polystyrene tiles. On pine wood board, decreasing ozone deposition velocities were measured with increasing ozone concentrations and with RH increasing in the range 30-50%. (C) 2006 Elsevier Ltd. All rights reserved.
引用
收藏
页码:3129 / 3138
页数:10
相关论文
共 21 条
[1]  
*AIRPARIF, 2005, BIL QUAL AIR 2004 IL
[2]  
Aoki T, 2005, INDOOR AIR 2005: PROCEEDINGS OF THE 10TH INTERNATIONAL CONFERENCE ON INDOOR AIR QUALITY AND CLIMATE, VOLS 1-5, P1552
[3]   Health effects of a mixture of indoor air volatile organics, their ozone oxidation products, and stress [J].
Fiedler, N ;
Laumbach, R ;
Kelly-McNeil, K ;
Lioy, P ;
Fan, ZH ;
Zhang, JF ;
Ottenweller, J ;
Ohman-Strickland, P ;
Kipen, H .
ENVIRONMENTAL HEALTH PERSPECTIVES, 2005, 113 (11) :1542-1548
[4]   Compilation of tables of surface deposition velocities for O3, NO2 and SO2 to a range of indoor surfaces [J].
Grontoft, T ;
Raychaudhuri, MR .
ATMOSPHERIC ENVIRONMENT, 2004, 38 (04) :533-544
[5]   The humidity dependence of ozone deposition onto a variety of building surfaces [J].
Grontoft, T ;
Henriksen, JF ;
Seip, HM .
ATMOSPHERIC ENVIRONMENT, 2004, 38 (01) :59-68
[6]   Dry deposition of ozone on building materials. Chamber measurements and modelling of the time-dependent deposition [J].
Grontoft, T .
ATMOSPHERIC ENVIRONMENT, 2002, 36 (36-37) :5661-5670
[7]  
Hubbard H, 2005, INDOOR AIR 2005: PROCEEDINGS OF THE 10TH INTERNATIONAL CONFERENCE ON INDOOR AIR QUALITY AND CLIMATE, VOLS 1-5, P2361
[8]   Determination of ozone removal rates by selected building products using the FLEC emission cell [J].
Kleno, JG ;
Clausen, PA ;
Weschler, CJ ;
Wolkoff, P .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2001, 35 (12) :2548-2553
[9]   Sensory evaluation of emissions from selected building products exposed to ozone [J].
Knudsen, HN ;
Nielsen, PA ;
Clausen, PA ;
Wilkins, CK ;
Wolkoff, P .
INDOOR AIR, 2003, 13 (03) :223-231
[10]   The rate of ozone uptake on carpets: Experimental studies [J].
Morrison, GC ;
Nazaroff, WW .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2000, 34 (23) :4963-4968