Influences of initial conditions and boundary conditions on regional and urban scale Eulerian air quality transport model simulations

Tsun-Hsien Liu , Fu-Tien Jeng , Ho-Chun Huang , Erik Berge , Julius S. Chang
{"title":"Influences of initial conditions and boundary conditions on regional and urban scale Eulerian air quality transport model simulations","authors":"Tsun-Hsien Liu ,&nbsp;Fu-Tien Jeng ,&nbsp;Ho-Chun Huang ,&nbsp;Erik Berge ,&nbsp;Julius S. Chang","doi":"10.1016/S1465-9972(00)00048-9","DOIUrl":null,"url":null,"abstract":"<div><p>Influences of initial and boundary conditions were quantified by analysis of a simplified governing equation followed with a tracer and O<sub>3</sub> simulations using a three-dimensional air quality transport model. The analytical solution derived from the governing equation indicated that the impacts of initial conditions on a given site decrease with simulation time and significantly affect the species concentrations before the arrival of the boundary conditions. Boundary influences, which decrease during the downwind transport, are significant to a selected site when the arrival time of boundary condition is short and the species lifetime is long.</p><p>Non-reactive tracers and O<sub>3</sub> were then added to SARMAP Air Quality Model (SAQM), a three-dimensional transport model, and the results showed that tracer lifetime and arrival time determine the boundary influences on a given site consistent with the analysis obtained from the governing equation. Moreover, boundary conditions followed initial conditions to affect the calculated ozone concentrations at a given site and the influences are proportional to the magnitude of the prescribed boundary conditions, arrival time, and are more obvious at local nighttime. When the arrival time is 15 h, an average of 64% of initial ozone boundary conditions will contribute to the calculated ozone concentrations. For arrival times of 23, 20, and 7 h, the ratios are 26%, 34%, and 79%, respectively. This study indicated that the derived analytical solution could be used by air quality modelers in estimating the boundary influences as long as the species lifetime are known.</p></div>","PeriodicalId":100235,"journal":{"name":"Chemosphere - Global Change Science","volume":"3 2","pages":"Pages 175-183"},"PeriodicalIF":0.0000,"publicationDate":"2001-04-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://sci-hub-pdf.com/10.1016/S1465-9972(00)00048-9","citationCount":"26","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Chemosphere - Global Change Science","FirstCategoryId":"1085","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S1465997200000489","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 26

Abstract

Influences of initial and boundary conditions were quantified by analysis of a simplified governing equation followed with a tracer and O3 simulations using a three-dimensional air quality transport model. The analytical solution derived from the governing equation indicated that the impacts of initial conditions on a given site decrease with simulation time and significantly affect the species concentrations before the arrival of the boundary conditions. Boundary influences, which decrease during the downwind transport, are significant to a selected site when the arrival time of boundary condition is short and the species lifetime is long.

Non-reactive tracers and O3 were then added to SARMAP Air Quality Model (SAQM), a three-dimensional transport model, and the results showed that tracer lifetime and arrival time determine the boundary influences on a given site consistent with the analysis obtained from the governing equation. Moreover, boundary conditions followed initial conditions to affect the calculated ozone concentrations at a given site and the influences are proportional to the magnitude of the prescribed boundary conditions, arrival time, and are more obvious at local nighttime. When the arrival time is 15 h, an average of 64% of initial ozone boundary conditions will contribute to the calculated ozone concentrations. For arrival times of 23, 20, and 7 h, the ratios are 26%, 34%, and 79%, respectively. This study indicated that the derived analytical solution could be used by air quality modelers in estimating the boundary influences as long as the species lifetime are known.

查看原文
分享 分享
微信好友 朋友圈 QQ好友 复制链接
本刊更多论文
初始条件和边界条件对区域和城市尺度欧拉空气质量输送模式模拟的影响
通过分析一个简化的控制方程,然后使用示踪剂和使用三维空气质量运输模型模拟O3,量化了初始条件和边界条件的影响。由控制方程导出的解析解表明,初始条件对给定地点的影响随模拟时间的延长而减小,在边界条件到达之前对物种浓度有显著影响。当边界条件到达时间较短、物种寿命较长时,边界层影响对选定地点的影响显著,在顺风运输过程中边界层影响减小。然后将非反应性示踪剂和O3加入到SARMAP空气质量模型(SAQM)中,该模型是一个三维输运模型,结果表明,示踪剂的寿命和到达时间决定了给定地点的边界影响,这与控制方程的分析结果一致。边界条件对给定地点臭氧浓度的影响紧随初始条件之后,其影响与边界条件的大小和到达时间成正比,且在当地夜间更为明显。当到达时间为15 h时,平均64%的初始臭氧边界条件对计算的臭氧浓度有贡献。到达时间为23、20和7 h时,比例分别为26%、34%和79%。该研究表明,只要物种寿命已知,导出的解析解可以被空气质量建模者用于估计边界影响。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
求助全文
约1分钟内获得全文 去求助
来源期刊
自引率
0.00%
发文量
0
期刊最新文献
Methane production and theoretical consumption in UK livestock production: is a realistic balance possible? Carbon sink in cropland soils and the emission of greenhouse gases from paddy soils: a review of work in China Modeling the biogeochemical cycle of dimethylsulfide in the upper ocean: a review On the performance of SF6 permeation tubes used in determining methane emission from grazing livestock An analysis of simulated and observed global mean near-surface air temperature anomalies from 1979 to 1999: trends and attribution of causes
×
引用
GB/T 7714-2015
复制
MLA
复制
APA
复制
导出至
BibTeX EndNote RefMan NoteFirst NoteExpress
×
×
提示
您的信息不完整,为了账户安全,请先补充。
现在去补充
×
提示
您因"违规操作"
具体请查看互助需知
我知道了
×
提示
现在去查看 取消
×
提示
确定
0
微信
客服QQ
Book学术公众号 扫码关注我们
反馈
×
意见反馈
请填写您的意见或建议
请填写您的手机或邮箱
已复制链接
已复制链接
快去分享给好友吧!
我知道了
×
扫码分享
扫码分享
Book学术官方微信
Book学术文献互助
Book学术文献互助群
群 号:481959085
Book学术
文献互助 智能选刊 最新文献 互助须知 联系我们:info@booksci.cn
Book学术提供免费学术资源搜索服务,方便国内外学者检索中英文文献。致力于提供最便捷和优质的服务体验。
Copyright © 2023 Book学术 All rights reserved.
ghs 京公网安备 11010802042870号 京ICP备2023020795号-1