首页> 外文会议>International Conference on Large-Scale Scientific Computing(LSSC 2005); 20050606-10; Sozopol(BG) >The Use of MM5-CMAQ for an Incinerator Air Quality Impact Assessment for Metals, PAH, Dioxins and Furans: Spain Case Study
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The Use of MM5-CMAQ for an Incinerator Air Quality Impact Assessment for Metals, PAH, Dioxins and Furans: Spain Case Study

机译:MM5-CMAQ在金属,多环芳烃,二恶英和呋喃的焚化炉空气质量影响评估中的应用:西班牙案例研究

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In this contribution we show the implementation of a modified version of MM5-CMAQ (Hutzell W.T., 2002) for carrying on an air quality impact analysis for installing an incinerator in the Basque Country Area (Spain). The modified CMAQ model (EPA USA, 2004) includes Poly-Chlorinated Dibenzo-p-Dioxins and Dibenzo-Furans (dioxins and furans). The model represents their cogeners as divided between gaseous and aerosol forms that exchange mass based on theoretical coefficients for gas to particle portioning. Modelled metals are included in CMAQ as part of the non-reactive aerosol component. Metals modelled are: As, Cd, Ni and Pb. In additional Benzo(a)pyrene (PAH) is also modelled. The model is implemented in a cluster platform in order to be used as a real-time air quality forecasting system by using the ON-OFF approach. The emissions of the projected incinerator in the ON run are incorporated by using the height of the chimney, the prescribed exit gas velocity, diameter of chimney and the limit emission values (worst scenario) prescribed in the Directive/2000/76/CE. The OFF run is done by using EMEP POP and PAH emission inventory. The system is mounted over one mother domain of 400 x 400 km with 9 km spatial resolution and two nesting levels: 100 km model domain with 3 km spatial resolution and 24 km with 1 km spatial resolution. All model domains have 23 vertical layers. The highest level is located at 100 mb. The architecture domain system is centered at the UTM coordinates assigned for the projected incinerator. EPER EU industrial emissions (May, 2004) of the surrounding large point industrial sources are used. Results are compared with the target values included in the proposal for a Directive of the European Parlament and of the Council (ENV 194 CODEC 439).
机译:在本文稿中,我们展示了MM5-CMAQ的修改版本(Hutzell W.T.,2002年)的实施,该版本用于对空气污染影响进行分析,以便在西班牙巴斯克地区安装焚化炉。改进的CMAQ模型(美国环境保护署,2004年)包括多氯化二苯并-对-二恶英和二苯并呋喃(二恶英和呋喃)。该模型代表了它们的热源,分为气态和气溶胶形式,它们根据气体对颗粒分配的理论系数交换质量。 CMAQ中包含建模金属,作为非反应性气溶胶成分的一部分。建模的金属为:砷,镉,镍和铅。另外,还对苯并(a)py(PAH)进行了建模。该模型在集群平台中实现,以便通过使用ON-OFF方法用作实时空气质量预测系统。通过使用烟囱的高度,规定的出口气体速度,烟囱的直径和Directive / 2000/76 / CE中规定的极限排放值(最坏的情况),将预计焚化炉在ON运行时的排放纳入其中。通过使用EMEP POP和PAH排放清单完成OFF运行。该系统安装在一个400 x 400 km的母域上,具有9 km的空间分辨率和两个嵌套级别:100 km的模型域具有3 km的空间分辨率,而24 km具有1 km的空间分辨率。所有模型域都有23个垂直层。最高级别位于100 mb。建筑领域系统以分配给投影焚化炉的UTM坐标为中心。使用了EPER欧盟的工业排放量(2004年5月),周围是大型工业排放源。将结果与《欧洲议会和理事会指令》提案(ENV 194 CODEC 439)中包含的目标值进行比较。

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