《外文翻译利用ArcGIS研究城市地区空气污染的空间造型.doc》由会员分享，可在线阅读，更多相关《外文翻译利用ArcGIS研究城市地区空气污染的空间造型.doc（16页珍藏版）》请在三一办公上搜索。
1、毕业设计(论文)文献翻译 利用ArcGIS研究城市地区 题 目 空气污染综合数据库开发 学 院 专 业 班 级 学 生 学 号 指导教师 二一一年六月七日Spatial Modelling of Air Pollution in Urban Areas withGIS: A Case Study on Integrated Database DevelopmentL. MatejicekInstitute for Environmental Studies, Charles University, Prague, 128 01, Czech Republic(lmatejicmbox.cesn
2、et.cz)Abstract: A wide range of data collected by monitoring systems and by mathematical and physical modelling can be managed in the frame of spatial models developed in the GIS. In addition to data management and standard environmental analysis of air pollution, data from remote sensing (aerial an
3、d satellite images) can extend all the data sets. In spite of that simulation of air pollutant distribution is carried out by standalone computer systems, the spatial database in the frame of the GIS is used to support decision-making processes in a more efficient way. Mostly, data are included in t
4、he map layers as attributes. Other map layers are carried out by the methods of spatial interpolation, raster algebra and case oriented analysis. A series of extensions is built in the GIS to adapt its functionality. As examples, the spatial models of the flat urban area and the street canyon with e
5、xtensive traffic polluted with NOx are constructed. Different scales of the spatial models require variant methods of construction, data management and spatial data sources. The measurement of NOx and O3 by the automatic monitoring system and data from the differential absorption LIDAR are used for
6、investigation of air pollution. Spatial data contain digital maps of both the areas complemented by digital elevation models. Environmental analyses represent spatial interpolations of air pollution that are displayed in horizontal and vertical plains. Case oriented analyses are mostly focused on ri
7、sk assessment methods. Finally, the LIDAR monitoring results and the results obtained by modelling and spatial analyses are discussed in the context of environmental management of the urban areas. The spatial models and their extensions are developed in the frame of the ESRIs ArcGIS and ArcView prog
8、ramming tools. Aerial and satellite images preprocessed by the ERDAS Imagine represent areas of Prague.Keywords: spatial modelling; GIS; air pollution; Lidar1. INTRODUCTIONThe recent development of spatial data management in the frame of geographic information systems (GISs) has created the new era
9、of environmental modelling. More powerful computers have made running air quality models at global and locale spatial scales possible. In order to understand the function of more complex models, the modelling system should consist of other subsystems (point and area sources of pollution, spatial des
10、cription of terrain elevations, meteorological data, air quality monitoring networks). Obviously, the use of the GIS has become essential in providing boundary conditions to the air quality models. Certainly, the use of the GIS in air pollution modelling can be extended moreover to processing the su
11、rface data. Many models have been coupled with the GIS in the past decade to simulate various environmental processes as described in the book written by Longley et al. 2001. Due to the four-dimensional nature of distribution of atmospheric pollutants, the concept of the GIS should be extended to in
12、clude temporal variations of three-dimensional spatial data. Considering to a huge volume of numerical calculations, two-dimensional interpolations into the horizontal layers are used to interpolate threedimensional atmospheric data onto a model grid system. The interpolations, integrations of land
13、cover surface data and the GIS analyses focused on small scale spatial models carried out in the kilometer grid are discussed by Lee in the book published by Goodchild 1996. In case of large scale air quality modelling, more detailed spatial data are needed to include the impact of buildings and oth
14、er man-made barriers on distribution of air pollutants, Janour, 1999; Civis 2001. Apart from this approach, the statistical theory is also used to indicate spatio-temporal interactions as described by Briggs et al. 2000.2. METHODS OF INTEGRATION AIR QUALITY MODELS INTO THE GISA few scenarios can be
15、established to integrate air quality models into the GIS. The basic level is represented by the standalone software application for simulation of air quality models (ISCST3, ISCPRIME), which is accompanied by data inputs and other software systems (GIS, RDBMS, Surfer, WWW-presentations). The individ
16、ual programs form heterogeneous data structures that require the transport of data into various data formats. Figure 1 illustrates an example of steps carried out during the simulation of air quality models.Figure 1. The standalone simulation of air quality models,which is extended by preprocessing
17、and postprocessing software systems. On the other side, a number of computer programs has been developed to integrated particular functions of the GIS, air quality modelling and graphic systems. Mostly, they are determined to carry out specific calculation without links to other software application
18、s. The GIS based software applications are mostly based on spatial software libraries. The missing functions (air quality modelling, visualisation tools) can be complemented or shared through the dynamiclink libraries. The integrated emission evaluation systems, which offer alternative ways of using
19、 the emission models together with selectedfunctionality of the GISs, are described by Rebolj 1999. A number of software applications is focused on design of relational databases and their interconnection together with standard air quality modelling systems. The structure of the programs developed w
20、ith spatial software libraries showsfigure 2. Software application Compiled routines from the GIS, modelling and graphic libraries(ArcObjects, AVENUE)Figure 2. The standalone software application for2.1 GIS data management and functionalityConsidering to the both described scenarios of integration,
21、the scope and scale of urban areas problems make the GIS a powerful tool for management of spatial and temporal data, complex analyses and visualization, Matejicek, 2002. Due to the ability to manage a number of spatial and temporal data formats, data structures created in the frame of the GISs open
22、 the ways to building air quality information systems that synthesize geospatial and temporal air quality data to support spatio-temporal analysis and dynamic modelling. There is also a growing amount of the digital maps in the GIS community, which are used to support decision-making processes of th
23、e urban authorities (data sets for land cover and climatic variables, digital elevation models, which are extended by blocks of buildings and trees, air pollution sources and monitoring networks, soil and hydrologic properties, road and railway networks). While much progress has been made with the m
24、apping of environmental data and the creation of national, regional and local data sets, many challenges remain. For example, air quality models are not used to be included into the GIS. As standalone software applications, they use various data formats, which can usually operate independently with
25、their own GIS database. Similarly, air quality management agencies are creating GIS data sets to support their operations without any data standards that can support spatio-temporal analysis and dynamic modelling. The common theme among these challenges is the need for integration of different spati
26、al and air quality data, integration of data and modelling, integration across spatial scales. The requirements for the integrated spatial modelling of air quality in the frame of the GIS represent a common geospatial coordinate system,vector themes (points, lines and areas) for description of surfa
27、ce objects (buildings, bridges, vegetation) supported by raster and TIN surface data (digital elevation models), vector themes for representation of air pollution inputs (local point, line and area sources of pollution, long-distance transport of air pollution). The key parts of the projects represe
28、nt data of air quality measured by monitoring networks, terrain measurements (LIDAR) and simulation results of air quality models.2.2 GIS data modelsNowadays, all the mentioned properties can accomplish a few of the GISs. In the presentedstudy, the ArcGIS distributed by the Environmental Systems Res
29、earch Institute (ESRI) has been used for the proposed operations. The ArcGIS, a descendant of the widely used ArcInfo,can manage spatial data in a few levels as shapefiles, coverages and geodatabases. Moreover the expansion of the ArcGIS functionality by the COM technology, the Visual Basic is the s
30、tandardinterface language, just as Microsoft uses the Visual Basic as the interface language for other software applications. The ArcGIS can be customized for particular applications of the GIS using specially designed data models. Currently, a number of data models have been published in hydrology
31、Maidment, 2002, biodiversity, forestry, etc. Air quality modelling can be accomplished by exchanging data between ArcGIS and the independent air quality simulation system, by constructing a simulation tools attached to a project in the ArcGIS, or by customizing the behavior of the ArcGIS objects. Th
32、e choice depends on the model complexity and calculation requirements in the frame of the various ArcGIS levels. All data are stored in the relational database, which can be represented on the basic level by the personal geodatabase (Microsoft Access), or by the RDBMS (Oracle, Microsoft SQL Server).
33、 So, the data transfer among other standalone software applications can be realized directly through the implemented database connections. In case of the ArcGISs geodatabase, all the data are loaded into the relational database, so that the geospatial coordinate data of the GIS data layers are store
34、d in the relational data tables. Since the relational database supports relationships between its tables, feature-to-feature spatial connections can be set up among the GIS data layers together with linking and joining of external data tables.2.3 SPATIAL MODELS FOR AIR QUALITY ASSESSMENT EXTENDED BY
35、 THE LIDAR MEASUREMENTSThe data required for spatial models to serve air quality modelling can be grouped into a few classes. Figure 3 shows spatial data included into map layers in the frame of a GIS projectFigure 3. Data included into GIS map layers.It is impossible to completely enumerate all the
36、 spatial and non-spatial data needed, since the more that is known, the better. However, the accuracy of the model results does not depend on the data alone. Choice of the appropriate modelling tools and their setting represents other key parts of air quality modelling. So, if the models do not requ
37、ire or are not capable of evaluating some detailed information, there is little benefit in putting that data in a GIS project. To examine the functionality of the spatial modelling system, the Industrial Source Complex-Short Term (ISCST3), its version with Plume Rise Enhancements (ISC-PRIME), and th
38、e AMS/EPA Regulatory Models (AERMOD/AERMOD-PRIME) have been included into the projects. The ISC-AERMOD View with its preprocessing and postprocessing modules has been used as the unified interface of the air dispersion models. The spatial surface data (digital elevation model- DEM, buildings) make u
39、p the input into the preprocessing modules (Import of the Digital terrain data in ISC-AERMOD, Building Profile Input Program-BPIP). Other surface data (bridges, trees, satellite and aerial images) complement spatial information for display and visualization. The layers with sources of pollution cont
40、ain (in addition to the coordinates and shapes) the attributes, which describe emission properties. The surface data and data about sources of pollution have to be transferred into appropriate input formats to run the air quality dispersion models. The primary storage in the GIS spatial database ser
41、ves furthermore for spatial analysis, display and visualization. Likewise the previous data, meteorological data are also preprocessed from the database storage into the input formats for air quality dispersion modelling. The map layers, which represent monitoring networks and LIDAR measurements, se
42、rve for a comparison of themeasured data with the predicted air pollution data calculated by the models. The mentioned air quality models are steady-state Gaussian plume models used to assess pollutant concentrations from a wide variety of sources mostly associated with an industrial complex. The st
43、eady state values of variables are transferred and incorporated into the GIS database, which can be handy to manage data time series. To accommodate large data and many variables such as air quality data, climatic data, properties of sources of pollution, the data repository containing all types of
44、time series data for all features and for all times is proposed. So, time series information can be depicted in 3-D space. The three coordinate axes mark space (S-identification code of a spatial future), time (T-discrete time) and variable being measured (V- identification code of a variable). The
45、data value indexed by the space, the time and the variable can be defined as D(S,T,V). Thus, each stored value is represented by a point in threedimensional space with its corresponding coordinates, figure 4. In order to extract time series, the space and variable coordinate have to be specified in
46、a query. The result is represented by selected records that match up to the condition in a query. Due to spatial properties of the GIS, space coordinates can be derived from a spatial query in the frame of GIS functionality. The associationsbetween data repository and spatial objects in the ArcGIS g
47、eodatabase are specified by relationships, which are stored into the relationship classes.Figure 4. Data repository with 3-D space indexes.4. CASE STUDIES OF THE URBAN AREASThe various data sets (digital maps, aerial and satellite images, spatio-temporal data in the 3-D database, data outputs from s
48、imulation systems) have been linked together to make up projects fordifferent spatial scales. The GIS, originally design to display 2-D digital maps, has been extended into 3-D mapping and data management in the frame of the ArcGIS. As examples, two urban areas of Prague have been used to demonstrat
49、e abilities of the spatial modelling.4.1 Spatial modelling of the flat urban areaThe inputs of spatial data represent digital elevation model, which can be used for air pollution modelling, and aerial or satellite images, which can serve for classification of the surface into classes to set the surface graini
