焚风对复杂地形中PM10浓度和城市边界层的影响:来自波兰Kraków的案例研究

Piotr Sekula, A. Bokwa, Z. Ustrnul, M. Zimnoch, B. Bochenek
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引用次数: 6

摘要

波兰Kraków是一个空气质量很差的城市,位于巨大的Wisła (Vistula)山谷,受到来自Tatra山脉的焚风的影响。我们分析了2017年9月至2018年4月和2018年9月至2019年4月期间的14个长周期的风。使用的数据包括来自地面站的PM10(即空气动力学直径高达10微米的颗粒物)浓度、空气温度和相对湿度、风速和风向的测量数据,以及高达100米a.g.l的桅杆测量数据,以及模型分析结果。一个非操作配置的AROME CMC(在中尺度规范模式配置的应用研究操作)1公里x 1公里的应用。提出了一个关于焚烧炉对城市空气污染影响的概念模型。焚风对PM10时空格局的特殊影响取决于其在城市中的传输方式:a.焚风在山谷上方流动,山谷上方有强冷空气池和回流;B.风从东部、较宽的部分或山谷顶部进入山谷,破坏冷空气池;C.由引力波产生的引力波足够强,可以进入山谷西部较窄的部分,并在城市内部造成较大的湍流参数空间差异。第一种转移模式恶化了全市空气污染扩散状况,导致PM10水平大幅上升(从低于50到150-200µg·m−3),第二种转移模式改善了扩散状况,导致全市PM10水平大幅下降(从150-200到50µg·m−3),第三种转移模式导致全市PM10水平存在较大的空间差异(50-70µg·m−3)。焚烧炉对空气污染扩散条件没有单一的影响。
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The impact of a foehn wind on PM10 concentrations and the urban boundary layer in complex terrain: a case study from Kraków, Poland
Abstract Kraków, Poland, is a city with poor air quality, located in the large Wisła (Vistula) valley, and affected by a foehn wind from the Tatra Mountains. We analyzed 14 long episodes of the foehn from the periods Sep 2017 - Apr 2018 and Sep 2018 - Apr 2019. Data used included measurements of PM10 (i.e. particulate matter with an aerodynamic diameter up to 10 µm) concentrations) concentrations, air temperature and relative humidity, wind speed and direction from ground stations and mast measurements up to 100 m a.g.l., along with model analysis results. A non-operational configuration of the AROME CMC (the Application of Research to Operations at Mesoscale canonical model configuration) 1 km x 1 km was applied. A conceptual model concerning the impact of a foehn on urban air pollution was developed. The occurrence of a particular effect of a foehn on the PM10 spatial-temporal pattern depends on its mode of transfer through the city: a. a foehn flows above the valley where a strong cold air pool and a return flow can be found; b. a foehn enters the valley from the eastern, wider part or from the valley top and destroys the cold air pool; c. gravity waves generated by a foehn are strong enough to enter the western narrower part of the valley and cause large spatial differences in turbulence parameters within the city. The first transfer mode worsens air pollution dispersion conditions throughout the city and leads to large increases in PM10 levels (from below 50 to 150-200 µg⋅m−3), the second mode improves dispersion and leads to large decreases in PM10 levels (from 150-200 to below 50 µg⋅m−3) throughout the city, and the third generates large spatial differences in PM10 levels (50-70 µg⋅m−3) within the city. There is no single effect of a foehn on air pollution dispersion conditions.
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