Five-year measurements of ozone fluxes to a Danish Norway spruce canopy

被引:62
作者
Mikkelsen, TN
Ro-Poulsen, H
Hovmand, MF
Jensen, NO
Pilegaard, K
Egelov, AH
机构
[1] Risoe Natl Lab, Plant Res Dept, DK-4000 Roskilde, Denmark
[2] Univ Copenhagen, Inst Bot, DK-1353 Copenhagen, Denmark
[3] Natl Environm Res Inst, DK-4000 Roskilde, Denmark
[4] Danish Forest & Landscape Inst, Dept Forest Ecol, DK-2970 Horsholm, Denmark
[5] Risoe Natl Lab, Wind Energy Dept, DK-4000 Roskilde, Denmark
关键词
canopy resistance; deposition; deposition velocity; O(3); stomatal uptake; Picea abies;
D O I
10.1016/j.atmosenv.2003.12.036
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Ozone concentrations and fluxes have been measured continuously during 5 years (1996-2000) by the gradient method in a Norway spruce dominated forest stand in West Jutland, Denmark, planted in 1965. The method has been validated against other methodologies and a relatively good relationship was found. The data are analysed to quantify diurnal, seasonal and yearly fluxes, and non-stomatal and stomatal removal are estimated. Monthly means of climatic data are shown, and day and night values of the aerodynamic resistance, r(a), viscous sub-layer resistance, r(b), and the surface or canopy resistance, r(c), are presented. The yearly ozone deposition is approximately 126 kg ha(-1). The canopy ozone uptake is highest during the day and during the summer. This is interpreted as increased stomatal uptake and physical and chemical reactions. The daily means of ozone concentration and fluxes averaged over 5 years correlate, but the correlation is primarily based on two different uncoupled processes outside and inside the stomates: (1) The ozone destruction in the canopy occurring outside the stomates is much influenced by temperature, light and humidity, e.g. surface reactions, NO- and VOC-emissions. (2) The same factors have a strong influence on the stomatal opening, e.g. midday and night closure. Thus, looking at diurnal variations, the diurnal ozone concentration and ozone flux do not correlate at all during the growing season. The maximum diurnal difference for the ozone concentration is a factor 1.3 and the maximum diurnal difference for the ozone flux is a factor 3. From dawn to ca. 8:00 the ozone deposition increases and the ozone concentration decreases. The yearly stomatal uptake of ozone is estimated to minimum 21% of the total deposition, being highest in May-August (30-33%) and lowest in November-February (4-9%). The physiological ozone uptake per leaf area is estimated to 0.33 g ozone m(-2) Y(-1). (C) 2004 Elsevier Ltd. All rights reserved.
引用
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页码:2361 / 2371
页数:11
相关论文
共 34 条
[1]   A CANOPY STOMATAL-RESISTANCE MODEL FOR GASEOUS DEPOSITION TO VEGETATED SURFACES [J].
BALDOCCHI, DD ;
HICKS, BB ;
CAMARA, P .
ATMOSPHERIC ENVIRONMENT, 1987, 21 (01) :91-101
[2]   Determination of the terpene flux from orange species and Norway spruce by relaxed eddy accumulation [J].
Christensen, CS ;
Hummelshoj, P ;
Jensen, NO ;
Larsen, B ;
Lohse, C ;
Pilegaard, K ;
Skov, H .
ATMOSPHERIC ENVIRONMENT, 2000, 34 (19) :3057-3067
[3]   Modelling of stomatal conductance and ozone flux of Norway spruce: comparison with field data [J].
Emberson, LD ;
Wieser, G ;
Ashmore, MR .
ENVIRONMENTAL POLLUTION, 2000, 109 (03) :393-402
[4]   DEPOSITION OF ATMOSPHERIC POLLUTANTS ON FORESTS [J].
FOWLER, D ;
CAPE, JN ;
UNSWORTH, MH .
PHILOSOPHICAL TRANSACTIONS OF THE ROYAL SOCIETY OF LONDON SERIES B-BIOLOGICAL SCIENCES, 1989, 324 (1223) :247-265
[5]   Measurements of ozone deposition to vegetation quantifying the flux, the stomatal and non-stomatal components [J].
Fowler, D ;
Flechard, C ;
Cape, JN ;
Storeton-West, RL ;
Coyle, M .
WATER AIR AND SOIL POLLUTION, 2001, 130 (1-4) :63-74
[6]  
FOWLER D, 1989, LIFE SCI R, V47, P189
[7]   Critical levels for ozone effects on vegetation in Europe [J].
Fuhrer, J ;
Skarby, L ;
Ashmore, MR .
ENVIRONMENTAL POLLUTION, 1997, 97 (1-2) :91-106
[8]   The exchange of ozone between vegetation and atmosphere:: micrometeorological measurement techniques and models [J].
Grünhage, L ;
Haenel, HD ;
Jäger, HJ .
ENVIRONMENTAL POLLUTION, 2000, 109 (03) :373-392
[9]   Patterns and mechanisms of transpiration in a large subalpine Norway spruce (Picea abies (L.) Karst.) [J].
Herzog, KM ;
Thum, R ;
Kronfuss, G ;
Heldstab, HJ ;
Hasler, R .
ECOLOGICAL RESEARCH, 1998, 13 (02) :105-116
[10]  
HOLMSGAARD E, 1977, FORSTLIGE FORSOGSVAE, V35, P161