The humidity dependence of ozone deposition onto a variety of building surfaces

被引:35
作者
Grontoft, T
Henriksen, JF
Seip, HM
机构
[1] Norwegian Inst Air Res, NO-2027 Kjeller, Norway
[2] Univ Oslo, Dept Chem, N-0315 Oslo, Norway
关键词
humidity; deposition velocity; modelling; surface reaction; ozone decomposition; calcareous stone; concrete;
D O I
10.1016/j.atmosenv.2003.09.043
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Measurements of the dry deposition Velocity of O-3 to material samples of calcareous stone, concrete and wood at varying humidity of the air, were performed in a deposition chamber. Equilibrium surface deposition velocities were found for various humidity values by fitting a model to the time-dependent deposition data. A deposition velocity-humidity model was derived giving three separate rate constants for the surface deposition velocities, i.e. on the dry surface, on the first mono-layer of adsorbed water and on additional surface water. The variation in the dry air equilibrium surface deposition velocities among the samples correlated with variations in effective areas, with larger effective areas giving higher measured deposition velocities. A minimum for the equilibrium surface deposition velocity was generally measured at an intermediate humidity close to the humidity found to correspond to one mono-layer of water molecules on the surfaces. At low air humidity the equilibrium surface deposition velocity of O-3 was found to decrease as more adsorbed water prevented direct contact of the O-3 molecules with the surface. This was partly compensated by an increase as more adsorbed water became available for reaction with O-3. At high air humidity the equilibrium surface deposition velocity was found to increase as the mass of water on the surface increased. The deposition velocity on bulk de-ionised water at RH = 90% was an order of magnitude lower than on the sample surfaces. (C) 2003 Elsevier Ltd. All rights reserved.
引用
收藏
页码:59 / 68
页数:10
相关论文
共 14 条
[1]  
[Anonymous], GUIDELINE POLLUTION
[2]  
Atkins P., 2014, Physical chemistry
[3]  
BRIMBLECOMBE P, 1988, ATMOSPHERIC ENV B, V24, P1
[4]   REMOVAL OF REACTIVE GASES AT INDOOR SURFACES - COMBINING MASS-TRANSPORT AND SURFACE KINETICS [J].
CANORUIZ, JA ;
KONG, D ;
BALAS, RB ;
NAZAROFF, WW .
ATMOSPHERIC ENVIRONMENT PART A-GENERAL TOPICS, 1993, 27 (13) :2039-2050
[5]   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
[6]  
GRONTOFT T, 2003, IN PRESS ATMOSPHERIC, DOI DOI 10.1016/J.ATMOSENV.2003.09.004
[7]   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
[8]  
Leygraf C, 2000, ELEC SOC S
[9]   DECOMPOSITION RATES OF OZONE IN LIVING AREAS [J].
MUELLER, FX ;
LOEB, L ;
MAPES, WH .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1973, 7 (04) :342-346
[10]  
NAZAROFF WW, 1993, AM SOC TEST MATER, V1205, P81, DOI 10.1520/STP13101S