Concentrations and decay rates of ozone in indoor air in dependence on building and surface materials

被引:26
作者
Moriske, HJ [1 ]
Ebert, G [1 ]
Konieczny, L [1 ]
Menk, G [1 ]
Schöndube, M [1 ]
机构
[1] Fed Environm Agcy, Inst Water Soil & Air Hyg, D-14195 Berlin, Germany
关键词
ozone; formaldehyde; indoor air pollution; building material; surface material;
D O I
10.1016/S0378-4274(98)00088-5
中图分类号
R99 [毒物学(毒理学)];
学科分类号
100405 ;
摘要
The decay of ozone in indoor air was measured in a closed chamber after contact with different building materials and residential surfaces. The tested materials were: vinyl wall paper, woodchip paper, plywood, latex paint, fitted carpet, and plaster. In the summer of 1996, the entry of ozone from ambient air into indoor air during ventilation and the ozone decay in indoor air, after windows had been closed again, were studied. Measurements were done in a residential house on the outskirts of Berlin. The following results were gained: the chamber measurements showed a decay of ozone after contact with most of the materials put inside the chamber. Higher decay rates have been obtained for wall papers, plywood, fitted carpet and plaster. As described in the literature, ozone is able to react with olefines inside the materials and is able to form formaldehyde and other components. This formation of formaldehyde could also be confirmed in our investigations. Thus, in most cases, the formaldehyde concentrations were lower than the German guideline value of 0.1 ppm. The formation of formaldehyde could be prevented when a special wall paper that was coated with activated carbon was used. In the house, a complete ozone diffusion into indoor air took place during ventilation within 30 min. After closing the windows, the ozone concentrations decreased to the basic level before ventilation within 60-90 min. (C) 1998 Elsevier Science Ireland Ltd. All rights reserved.
引用
收藏
页码:319 / 323
页数:5
相关论文
共 12 条
[1]  
*BGBL, 1995, GES AND BUND IMM 19
[2]  
Geisling K.L., 1982, ENVIRON INT, V8, P153
[3]   Carbonyl products of the gas-phase reaction of ozone with 1-alkenes [J].
Grosjean, E ;
Grosjean, D .
ATMOSPHERIC ENVIRONMENT, 1996, 30 (24) :4107-4113
[4]  
JAKOBI G, 1997, ANN METEOROL, V33, P66
[5]  
MORISKE HJ, 1995, P HLTH BUILD 1995 MI, V1, P537
[6]   DECOMPOSITION RATES OF OZONE IN LIVING AREAS [J].
MUELLER, FX ;
LOEB, L ;
MAPES, WH .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1973, 7 (04) :342-346
[7]  
PRESCHER KE, 1983, GESUNDHEITS INGENIEU, V104, P198
[8]   MODELING OZONE DEPOSITION ONTO INDOOR RESIDENTIAL SURFACES [J].
REISS, R ;
RYAN, PB ;
KOUTRAKIS, P .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1994, 28 (03) :504-513
[9]   OZONE REACTIVE CHEMISTRY ON INTERIOR LATEX PAINT [J].
REISS, R ;
RYAN, PB ;
KOUTRAKIS, P ;
TIBBETTS, SJ .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1995, 29 (08) :1906-1912
[10]  
*UMW, 1997, DAT UMW AUSG 97