Methodology for direct field measurements of ozone flux to foliage with shoot chambers

被引:43
作者
Altimir, N
Vesala, T
Keronen, P
Kulmala, M
Hari, P
机构
[1] Univ Helsinki, Dept Forest Ecol, FIN-00014 Helsinki, Finland
[2] Univ Helsinki, Dept Phys, FIN-00014 Helsinki, Finland
关键词
deposition dry; Scots pine; signal-noise ratio; wall-loss; cuvette;
D O I
10.1016/S1352-2310(01)00478-2
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Values of ozone (O-3) flux measured on the shoot scale by enclosure techniques can provide detailed information about the partition and seasonality of the removal pathways on the foliage. However, O-3 reactivity makes such measurements potentially inaccurate, particularly in field conditions where ambient concentration is low. Special consideration should be given to the losses on the chamber wall material, which can rival in magnitude and dynamics the measure of shoot removal. We propose a way of taking into account this dynamic behaviour in the context of field monitoring with simple chambers based on dynamic principles. We accommodated an existing field monitoring gas exchange system for CO2 and water vapour to measure simultaneous, but independent, O-3 fluxes. We report here the system's performance based on the analysis of 19-month data. The background noise of the measurements is mainly imposed by the analyser and is around 2 mug m(-3). The resolution of the system is in the order of 10(-2)mug m(-2) s(-1). The disturbance due to wall-losses was corrected thoroughly but it was mostly needed when the shoot activity was low and the mass flow signals produced by the shoots and the walls came close to each other. In spite of the disfavouring combination of chamber material, O-3 reactivity and low concentrations, we have successfully followed diurnal and seasonal trends Of O-3 removal in Scots pine foliage. (C) 2002 Elsevier Science Ltd. All rights reserved.
引用
收藏
页码:19 / 29
页数:11
相关论文
共 32 条
[1]  
Aalto Tuula, 1998, Silva Fennica, V32, P321
[2]   Variations and vertical profiles of trace gas and aerosol concentrations and CO2 exchange in Eastern Lapland [J].
Ahonen, T ;
Aalto, P ;
Rannik, U ;
Kulmala, M ;
Nilsson, ED ;
Palmroth, S ;
Ylitalo, H ;
Hari, P .
ATMOSPHERIC ENVIRONMENT, 1997, 31 (20) :3351-3362
[3]   INJURY RESPONSE OF PHASEOLUS-VULGARIS TO OZONE FLUX-DENSITY [J].
AMIRO, BD ;
GILLESPIE, TJ ;
THURTELL, GW .
ATMOSPHERIC ENVIRONMENT, 1984, 18 (06) :1207-1215
[4]  
BURKE KA, 1994, COLUMBIA J LAW SOC P, V28, P1
[5]  
Catsky J., 1971, PLANT PHOTOSYNTHETIC, P49
[6]  
Cieslik S., 1997, Biosphere-atmosphere exchange of pollutants and trace substances: experimental and theoretical studies of biogenic emissions and of pollutant deposition., P225
[7]   CANOPY SCALE MEASUREMENTS OF STOMATAL AND CUTICULAR O-3 UPTAKE BY SITKA SPRUCE [J].
COE, H ;
GALLAGHER, MW ;
CHOULARTON, TW ;
DORE, C .
ATMOSPHERIC ENVIRONMENT, 1995, 29 (12) :1413-1423
[8]   COMPENSATING FOR SINK EFFECTS IN EMISSIONS TEST CHAMBERS BY MATHEMATICAL-MODELING [J].
DUNN, JE ;
TICHENOR, BA .
ATMOSPHERIC ENVIRONMENT, 1988, 22 (05) :885-894
[9]   A GAS-EXCHANGE SYSTEM TO STUDY THE EFFECTS OF LEAF SURFACE WETNESS ON THE DEPOSITION OF OZONE [J].
FUENTES, JD ;
GILLESPIE, TJ .
ATMOSPHERIC ENVIRONMENT PART A-GENERAL TOPICS, 1992, 26 (06) :1165-1173
[10]   DRY DEPOSITION TO PINE OF SULFUR-DIOXIDE AND OZONE AT LOW CONCENTRATION [J].
GRANAT, L ;
RICHTER, A .
ATMOSPHERIC ENVIRONMENT, 1995, 29 (14) :1677-1683