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Evaluating the calculated dry deposition velocities of reactive nitrogen oxides and ozone from two community models over a temperate deciduous forest

机译:从温带落叶林的两个群落模型估算反应性氮氧化物和臭氧的干沉降速度

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摘要

Hourly measurements of O_3, NO, NO_2, PAN, HNO_3 and NOy concentrations, and eddy-covariance fluxes of O_3 and NOj, over a temperate deciduous forest from June to November, 2000 were used to evaluate the dry deposition velocities (V_d) estimated by the WRF-Chem dry deposition module (WDDM), which adopted Wesely (1989) scheme for surface resistance (Rc), and the Noah land surface model coupled with a photosynthesis-based Gas-exchange Evapotranspiration Model (Noah-GEM). Noah-GEM produced better V_d(O_3) variations due to its more realistically simulated stomatal resistance (R_s) than WDDM. V_d(O_3) is very sensitive to the minimum canopy stomatal resistance (Ri) which is specified for each seasonal category assigned in WDDM. Treating Sep-Oct as autumn in WDDM for this deciduous forest site caused a large underprediction of V_d(O_3) due to the leafless assumption in 'autumn' seasonal category for which an infinite R_j was assigned. Reducing Rj to a value of 70 s m~1, the same as the default value for the summer season category, the modeled and measured V_d(O_3) agreed reasonably well. HNO_3 was found to dominate the NO_y, flux during the measurement period; thus the modeled V_d(NO_y) was mainly controlled by the aerodynamic and quasi-laminar sublayer resistances (R_a and Rb), both being sensitive to the surface roughness length (zo). Using an appropriate value for z_0 (10% of canopy height), WDDM and Noah-GEM agreed well with the observed daytime V_d(NO_y). The differences in V_d(HNO_3) between WDDM and Noah-GEM were small due to the small differences in the calculated R_a and R_b between the two models; however, the differences in R_c of NO_2 and PAN between the two models reached a factor of 1.1-1.5, which in turn caused a factor of 1.1-1.3 differences for V_d- Combining the measured concentrations and modeled V_d. NO,,, PAN and HNO_3 accounted for 19%, 4%, and 70% of the measured NO_y fluxes, respectively.
机译:利用2000年6月至11月在温带落叶林上每小时测量的O_3,NO,NO_2,PAN,HNO_3和NOy浓度以及O_3和NOj的涡率协方差通量,来评估由以下方法估算的干沉降速度(V_d): WRF-Chem干法沉积模块(WDDM),采用了Wesely(1989)方案的表面电阻(Rc),并将Noah陆地表面模型与基于光合作用的气体交换蒸发蒸腾模型(Noah-GEM)结合在一起。由于Noah-GEM比WDDM更真实地模拟了气孔阻力(R_s),因此产生了更好的V_d(O_3)变化。 V_d(O_3)对为WDDM中分配的每个季节性类别指定的最小冠层气孔阻力(Ri)非常敏感。由于在“秋季”季节类别中无叶假设并为其分配了无穷大的R_j,因此将该落叶林站点在WDDM中将Sep-Oct视为秋季,导致了V_d(O_3)的低估。将Rj降低到70 s m〜1的值(与夏季类别的默认值相同),建模和测量的V_d(O_3)相当吻合。发现在测量期间,HNO_3占主导地位的NO_y通量。因此,模型化的V_d(NO_y)主要受空气动力学和准层状亚层电阻(R_a和Rb)控制,两者都对表面粗糙度长度(zo)敏感。使用适当的z_0值(树冠高度的10%),WDDM和Noah-GEM与观察到的白天V_d(NO_y)很好地吻合。 WDDM和Noah-GEM之间的V_d(HNO_3)差异很小,这是因为两个模型之间的计算R_a和R_b差异很小;但是,两个模型之间NO_2和PAN的R_c差异达到了1.1-1.5的系数,这又导致V_d产生了1.1-1.3的差异-结合了所测量的浓度和建模的V_d。 NO,PAN和HNO_3分别占所测NO_y通量的19%,4%和70%。

著录项

  • 来源
    《Atmospheric environment》 |2011年第16期|p.2663-2674|共12页
  • 作者单位

    School of Environmental Science and Engineering. Sun Yat-sen University, Guangzhou 510275, China,Guangdong Provincial Key Laboratory of Environmental Pollution Control and Remediation Technology, Guangzhou 510275, China;

    School of Environmental Science and Engineering. Sun Yat-sen University, Guangzhou 510275, China;

    National Center for Atmospheric Research, Boulder, CO 80307, USA;

    National Center for Atmospheric Research, Boulder, CO 80307, USA;

    National Center for Atmospheric Research, Boulder, CO 80307, USA;

    Purdue University, West Lafayette, IN 47907, USA;

    Purdue University, West Lafayette, IN 47907, USA;

    School of Environmental Science and Engineering. Sun Yat-sen University, Guangzhou 510275, China;

    School of Engineering and Applied Sciences and Department of Earth and Planetary Sciences, Harvard University, Cambridge, MA 02138, USA;

    Atmospheric Modeling and Analysis Division, US Environmental Protection Agency, Research Triangle Park, NC 27711, USA;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    reactive nitrogen oxides; ozone; dry deposition velocity; wrf-chem dry deposition module; noah-gem; 1-d model;

    机译:反应性氮氧化物臭氧干沉积速度WRF化学干法沉积模块Noah-gem 1-d模型;

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