1A.4 Evaluation and Improvement of Dry Deposition Algorithms

Monday, 7 January 2019: 9:15 AM
North 124A (Phoenix Convention Center - West and North Buildings)
Leiming Zhang, ECCC, Toronto, Canada; and Z. Wu and Z. He

The first study quantifies differences between dry deposition algorithms commonly used in North America. Five models were selected to calculate dry deposition velocity (Vd) for O3 and SO2 over a temperate mixed forest in southern Ontario, Canada where a five-year flux database had previously been developed. Differences in mean Vd values between models were on the order of a factor of 2 in both summer and winter. Several models produced magnitudes of the diel variation of Vd(O3) comparable to the measurements, while all models produced slightly smaller diel variations than the measurements of Vd(SO2) in summer. A few models produced larger diel variations than the measurements of Vd for O3 and SO2 in winter. Model differences were mainly due to different surface resistance parameterizations for stomatal and non-stomatal uptake pathways, while differences in aerodynamic and quasi-laminar resistances played only a minor role. Modeled Vd in summer was sensitive to the minimum stomatal resistance and, in winter, to the canopy snow cover fraction. It is recommended that users of inferential dry deposition models consider an uncertainty factor of 2 or use ensemble modeling results for ecosystem assessment analysis.

The second study extends the gaseous dry deposition algorithm of Zhang et al. (2003) to include additional 14 oxidized volatile organic compounds (oVOC). Model parameters were selected mainly based on oVOC’s physical and chemical properties, and to some extent also based on limited flux measurements over a mixed forest. The model captured well the diel cycles of the observed Vd for most chemical species. Modeled Vd were comparable to the measurements for most of the oVOCs during the nighttime, but were lower during the daytime, e.g., with the maximum daytime Vd typically at 1 cm/s from the model versus 2-5 cm/s from the measurement. The very high Vd from measurements could be partially due to fast chemical reactions within the canopy, and the model is designed to provide relatively conservative estimates of Vd for most oVOC species, considering the flux data are still very limited. Based on the knowledge obtained from the model evaluations, model parameters for the 22 previously model oVOC species were also adjusted to slightly increase their Vd.

The third study revises a widely used size-resolved particle dry deposition algorithm of Zhang et al. (2001). The original model is able to reasonably predict Vd for bulk PM2.5 and PM10, but tends to overpredict Vd for particles smaller than 0.1 µm, especially over smooth surfaces. A revision is proposed to reduce the collection efficiencies by Brownion diffusion for most LUCs and increasing interception collection efficiencies for forest canopies so the modelled Vd can better fit field data over most of the land types. Such a modification may not have significant impact on the predicted bulk aerosol mass concentration, but has important implications to aerosol number concentration, which is of concern in studying climate-related issues.

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