Measurements of ozone deposition to vegetation quantifying the flux, the stomatal and non-stomatal components

被引:120
作者
Fowler, D [1 ]
Flechard, C [1 ]
Cape, JN [1 ]
Storeton-West, RL [1 ]
Coyle, M [1 ]
机构
[1] Ctr Ecol & Hydrol Edinburgh, Penicuik EH26 0QB, Midlothian, Scotland
关键词
AOT(40); deposition velocity; non-stomatal deposition; ozone; stomatal uptake;
D O I
10.1023/A:1012243317471
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Ozone deposition to vegetation represents the major sink for boundary layer ozone and yet the underlying mechanism of reaction and uptake at the surface is poorly understood. While overall rates Of O-3 deposition are known, the fractions of the flux absorbed by stomata and deposited to non-stomatal surfaces in the field have been poorly quantified. This paper reports 4 years of continuous fluxes by micrometeorological methods to moorland vegetation in southern Scotland. The flux has been partitioned between stomatal and non-stomatal fluxes and shows over a seasonal scale that the non-stomatal deposition (50 kg O-3 ha(-1) y(-1)) dominates the overall flux (77 kg O-3 ha(-1) y(-1)) and represents 70% of the total deposition. The surface resistance for non-stomatal O-3 deposition (r(ns)) decreases with temperature from 400 s m(-1) at 0 degreesC to 200 s m(-1) at 15 degreesC in dry conditions and is consistent with thermal decomposition of ozone at the surface with an apparent activation energy of about 36 kJ mole(-1). The 4 years of continuous flux measurements show that stomatal conductance, when O-3 concentrations are 80 mug m(-3), is substantially smaller than for smaller O-3 concentrations, although whether this is a response to VPD or O-3 remains unclear.
引用
收藏
页码:63 / 74
页数:12
相关论文
共 24 条
  • [1] [Anonymous], VEGETATION ATMOSPHER
  • [2] A CANOPY STOMATAL-RESISTANCE MODEL FOR GASEOUS DEPOSITION TO VEGETATED SURFACES
    BALDOCCHI, DD
    HICKS, BB
    CAMARA, P
    [J]. ATMOSPHERIC ENVIRONMENT, 1987, 21 (01) : 91 - 101
  • [3] CANOPY SCALE MEASUREMENTS OF STOMATAL AND CUTICULAR O-3 UPTAKE BY SITKA SPRUCE
    COE, H
    GALLAGHER, MW
    CHOULARTON, TW
    DORE, C
    [J]. ATMOSPHERIC ENVIRONMENT, 1995, 29 (12) : 1413 - 1423
  • [4] THE INTERPRETATION OF MEASUREMENTS OF SURFACE EXCHANGE OF NITROGEN-OXIDES - CORRECTION FOR CHEMICAL-REACTIONS
    DUYZER, JH
    DEINUM, G
    BAAK, J
    [J]. PHILOSOPHICAL TRANSACTIONS OF THE ROYAL SOCIETY A-MATHEMATICAL PHYSICAL AND ENGINEERING SCIENCES, 1995, 351 (1696): : 231 - 248
  • [5] Modelling of stomatal conductance and ozone flux of Norway spruce: comparison with field data
    Emberson, LD
    Wieser, G
    Ashmore, MR
    [J]. ENVIRONMENTAL POLLUTION, 2000, 109 (03) : 393 - 402
  • [6] Modelling stomatal ozone flux across Europe
    Emberson, LD
    Ashmore, MR
    Cambridge, HM
    Simpson, D
    Tuovinen, JP
    [J]. ENVIRONMENTAL POLLUTION, 2000, 109 (03) : 403 - 413
  • [7] The atmospheric budget of oxidized nitrogen and its role in ozone formation and deposition
    Fowler, D
    Flechard, C
    Skiba, U
    Coyle, M
    Cape, JN
    [J]. NEW PHYTOLOGIST, 1998, 139 (01) : 11 - 23
  • [8] Modelling photochemical oxidant formation, transport, deposition and exposure of terrestrial ecosystems
    Fowler, D
    Cape, JN
    Coyle, M
    Smith, RI
    Hjellbrekke, AG
    Simpson, D
    Derwent, RG
    Johnson, CE
    [J]. ENVIRONMENTAL POLLUTION, 1999, 100 (1-3) : 43 - 55
  • [9] Critical levels for ozone effects on vegetation in Europe
    Fuhrer, J
    Skarby, L
    Ashmore, MR
    [J]. ENVIRONMENTAL POLLUTION, 1997, 97 (1-2) : 91 - 106
  • [10] GALBALLY IE, 1971, Q J ROY METEOR SOC, V97, P18, DOI 10.1002/qj.49709741103