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CAMx4 Model Performance for Ozone in the UpperMidwest over the Summers of 2001, 2002, and 2003

机译:2001年,2002年和2003年夏季中西部上空臭氧的CAMx4模型性能

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The United States Environmental Protection Agency (EPA) recently promulgateddesignations for the 8-hour ozone National Ambient Air Quality Standard on April 15,2004 (69 CFR 23858, April 30, 2004). State Implementation Plans will include resultsfrom 3-D Eulerian photochemical transport models. In the past, these models wereapplied to short episodes with a few days used to “spin-up” the model simulation toreduce the impact of initial concentrations. Advancement in computer technology nowallows for the application of photochemical models over large domains and entiresummer seasons. This approach will better account for regional transport and minimizeany influence from initial concentrations.Several photochemical models treat the physical processes and chemistry that formozone. The Comprehensive Air Quality Model with Extensions (CAMx4) is applied toJune through August for 2001, 2002, and 2003. The photochemical modeling domainconsists of a 36 km grid over the Central and Eastern United States and a two-way nested12 km grid over the Upper Midwest.Operational evaluation for ozone modeling purposes includes evaluating model estimatesagainst observed 8 hr averaged ozone. The summers of 2001, 2002, and 2003 will beused for ozone strategy development to capture the variety of high ozone episodes thatoccur across the Upper Midwest.The modeling system predicts the spatial patterns of ozone concentrations over the LakeMichigan and Ohio Valley region quite well for all 3 summer seasons. Interestingregional spatial biases are also noted in the modeling, particularly in the Chicago area.The modeling system tends to over-predict low concentrations of 8 hr ozone and slightlyunder-predict the highest concentrations of 8 hr ozone in the Upper Midwest. Thevariability in performance from one summer to the next is minimal. Performancedegradation in particular regions of the domain seem more influenced by static inputs,such as emissions, than the changing meteorological inputs. Overall, the modeling systemperforms within EPA guidelines for the metrics used to characterize performance.
机译:美国环境保护局(EPA)最近于2004年4月15日发布了8小时臭氧国家环境空气质量标准的名称(69 CFR 23858,2004年4月30日)。州实施计划将包括3-D欧拉光化学迁移模型的结果。过去,将这些模型应用于短情节,而几天则用于“加速”模型仿真,以减少初始浓度的影响。计算机技术的进步现在允许在大范围和整个夏季使用光化学模型。这种方法将更好地说明区域迁移,并最小化初始浓度的任何影响。几种光化学模型可以处理形成甲醛的物理过程和化学反应。具有扩展功能的综合空气质量模型(CAMx4)于2001年,2002年和2003年的6月至8月应用。光化学建模域由美国中部和东部的36 km网格和上部的2层嵌套12 km网格组成。中西部地区:为进行臭氧建模而进行的业务评估包括针对观测到的8小时平均臭氧进行模型评估。 2001年,2002年和2003年夏天将用于制定臭氧战略,以捕获整个中西部上空发生的各种高臭氧事件。模型系统预测密歇根湖和俄亥俄州谷地区臭氧浓度的空间分布对所有人都非常有利3个夏季。在模型中还注意到了有趣的区域空间偏差,特别是在芝加哥地区。模型系统倾向于高估中西部上空8小时臭氧的低浓度,而略微低估最高8小时臭氧的浓度。从一个夏天到下一个夏天的表现差异很小。与变化的气象输入相比,该领域特定区域的性能下降似乎更受静态输入(例如排放)的影响。总体而言,建模系统在EPA准则内执行用于表征性能的指标。

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