GIS环境下上海市机动车尾气污染研究
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摘要
近年来,我国城市大气污染日趋严重,正在从燃煤型污染向交通型污染转变。目前全国机动车保有量迅速增长,尤其是北京、上海、广州等特大城市尤其明显。加之国产汽车单车排放水平比美国、日本要高出几倍甚至几十倍,汽车维修保养不善,城市交通道路拥堵和市内居民集中,这势必引起城市空气质量的不断恶化。因此定量计算上海市机动车尾气污染物排放状况,对汽车尾气排放的时间变化、车型差异及区域差异进行分析,并利用GIS系统所提供的城市路网、地理环境等信息,根据交通流量、气象条件,采用先进的机动车尾气扩散模型及数值计算方法,模拟交通污染扩散状况,为政府有关部门制定环境管理制度、合理制定城市规划和建设管理提供决策依据,具有重要的实用价值。
     本论文首先对上海市交通状况进行了大范围的调查、采样,建立了全市机动车保有量、车型比例、车公里数及车速清单。排放因子是计算道路机动车污染物排放强度的关键参数,它的确定直接影响到计算结果的准确性。本文采用美国的MOBILE6汽车排放因子模型计算了机动车排放因子,并结合新车排放因子测试数据及上海市机动车排放实际状况进行修正,最终建立了排放因子清单。在此基础上,分宏观、微观两条路线对全市机动车尾气污染物的排放状况进行定量评估。
     宏观上,对全市机动车排放污染物的总量分区域、车型及年份分别计算,据此可以分析机动车尾气污染物排放的时间变化、区域差异及车型差异。在区域上,将上海市划分为内环线内浦西、内环线内浦东、内外环间浦西、内外环间浦东及外环以外五个区域;车型上将上海市机动车划分为轻型汽油车、中型汽油车、中型柴油车、重型汽油车、重型柴油车、摩托车及轻型摩托车7类;在时间上计算了基准年2000年、现状年2002年及未来年至2020年排放状况。
     微观上,首先计算了上海市典型道路的线源源强,从中可以了解污染严重的路段。然后通过调查上海市21个典型交叉路口的车流状况,计算了路口的污染物排放。最后利用美国加利福尼亚交通部开发的线源空气质量模型CALINE4模式对典型道路污染物的扩散状况进行了模拟。
     在以上工作的基础上,采用Visual Basic6.0面向对象式编程语言、MapObjects2.1控件开发了上海市交通污染控制管理信息系统,集成了上述功能,并在GIS图形上进行直观显示。系统还就国内外排放控制措施进行对比,可为政府有关部门制定道路交通污染管理制度、合理制定城市规划和建设管理决策提供理论依据。
In recent years, the atmospheric pollution has been gradually more serious, which is transforming from coal-based pollution into traffic-based pollution. The number of motor vehicles in our whole country, especially in such metropolitan cities as Beijing, Shanghai and Guangzhou, increases rapidly. Furthermore, the emission level of vehicles made in China is tens or even hundreds times of that in the United States and Japan. The improvement and maintenance of vehicles are not quite good, urban traffic is very crowded and the population density is quite high, which deteriorate the urban air quality. Therefore, it is quite necessary to calculate the emission amount of vehicle exhaust pollutants and analyze its variation with time, vehicle types and area. Moreover, we applied an advanced line source dispersion model into the analysis of traffic pollutants distribution, by using the urban road net, geographic environment, traffic volume and meteorological conditions provided by GIS. All of the work is of great value as a basis for government to establish environment management system, urban planning and construction management.
    Firstly, we made a large-scale research and sampling on Shanghai traffic condition, based on which the inventory of vehicle type ratios, vehicle miles traveled and vehicle speeds were set up. Emission factor is a key parameter in the calculation of vehicle pollutants emission amount and emission rate. It directly influences the veracity of calculation results. In this research, we selected the MOBILE6 mobile source emission factor model provided by US EPA to calculate the vehicle emission factors, which were further modified according to the emission factors test data and Shanghai current situation. Thus, the inventory of emission factors was built up. Based on these inventories, we launched researches on Shanghai vehicle pollutants emission in two ways: macro-scale and micro-scale.
    In macro-scale research, we calculated the total emission amount according to areas, vehicle types and different years. Thus, we can get the emission difference with years, vehicle types and areas. The whole Shanghai city is divided into five sub-areas: region which lies to the west of Huangpu River and within inner-ring road; region which lies to the east of Huangpu River and within inner-ring road; region which lies
    
    
    
    to the west of Huangpu River and between the inner-ring road and outer-ring road; region which lies to the east of Huangpu River and within inner-ring road and region which lies outside the outer-ring road. All vehicles in Shanghai are divided into seven types: Light-duty gasoline vehicle, Medium-duty gasoline vehicle, Medium-duty diesel vehicle, Heavy-duty gasoline vehicle, Heavy-duty diesel vehicle, Motorcycle and Light duty motorcycle. The research time includes base year 2000, current year 2002 and future years of 2005,2010 and 2020.
    In micro-scale research, we calculated the line source emission rate of typical roads in Shanghai, from which we can learn the pollution situation of roads. We calculated emission amount of pollutants at 21 typical intersections base on survey of the vehicle flow, vehicle type ratio and vehicle speed. The dispersion situation along typical roads was simulated using the line source dispersion model-CALINE4, developed by California traffic department and recommended by USEPA.
    Base on the above researches, a Shanghai Traffic Pollution Management System was developed using Visual Basic 6.0 programming language and MapObjects 2.1. This system integrates all these functions and can display the modeling results on Shanghai traffic map. It also provides the comparison of vehicle exhaust control measures between China and other countries, which is a theoretical basis for government to set up traffic pollution management regulation and urban planning.
引文
[1] 陈长虹等,上海市机动车排气污染负荷的估算,上海环境科学,1997,16(6):26~29
    [2] 陈长虹等,上海市机动车排污状况与污染控制战略,1997,16(1):28~31
    [3] 邓顺熙,陈爱峡,曹申存,高速公路汽车污染物排放因子的测试与研究,中国公路学报,1999,12(增):94~100
    [4] 范秀英,张微,韩圣惠,我国汽车尾气污染状况及控制对策分析,环境科学,1999,20(5):102~108
    [5] 冯立权,田卫,余穆清 GIS在环境影响评价中的应用探析 遥感技术与应用,2001(16)4:270~273
    [6] 伏晴艳,陈小鸿,薛美根等,上海“十五”机动车发展与污染防治实施方案,2001
    [7] 伏晴艳,上海市空气中NO_x的污染现状及分担率,上海环境科学,2001,20(5):224~226
    [8] 傅立新,贺克斌等,MOBILE汽车源排放因子计算模式研究,环境科学学报,1997,17(4):474~479
    [9] 傅立新等,北京市机动车污染物排放特征,环境科学,2000,21(3):68~70
    [10] 郝吉明,傅立新等,城市机动车排放污染控制——国际经验分析与中国的研究成果,北京,中国环境科学出版社,2001
    [11] 何东全,郝吉明,傅立新。中国城市机动车污染挑战与对策[A],清华大学发展研究文集[C],北京:清华大学出版社,1998:145~149
    [12] 贾艳杰,我国大城市汽车废气污染问题及其治理对策 人文地理 1997,12(3):48
    [13] 金均,周安国等,公路汽车尾气扩散模式研究,上海环境科学,1997,16(10):18~21
    [14] 康嘉平等 基于GIS的北京市机动车污染数据库的开发和应用.环境科学 2000,21(6):95~97
    [15] 乐致威等,上海市NO_x分布状况及其影响因素,上海环境科学,1997,16(6):22~25
    [16] 李本纲,陶澎 地理信息系统在环境模型研究中的应用[J].环境科学,1998,19(3):87~90
    [17] 李莉,束炯,李朝颐等,上海市氮氧化物污染与气象条件关系特征分析,安全与环境学报,2004,4(1):36~39
    [18] 李莉,束炯,伏晴艳,基于GIS的机动车污染排放管理信息系统——上海案例应用,上海环境科学,2003,22(增):153~158,163
    [19] 李修刚等,用于城市交通规划的机动车污染物现状排放因子研究,交通运输工程学报,2001,1(4):87~91
    [20] 李修刚,基于GIS的城市交通大气环境模拟研究,东南大学(博士学为论文),1999(12)
    [21] 刘恩栋,武汉市机动车排放因子的确定,环境与开发,2000,15(3):36~45
    [22] 刘震等,三“S”一体化技术和方法的探讨,环境遥感,l995:152~160
    
    
    [23] 陆书玉,上海市机动车污染物及其控制对策,上海环境科学,1998,17(3):1~3
    [24] 鲁小琴,束炯,王铮,数据仓库在城市环境管理中的应用,东北测绘,2002,25(4):26~30,36
    [25] 罗澎,何龙等,建立深圳市机动车氮氧化物排放因子初探,中国环境监测,2000,16(4):7~12
    [26] 美国国家环保局,National Air Quality and Emissions Trends Report Appendix A, 2003.2
    [27] 束炯,李莉,张玮,大气污染对城市能见度影响研究的理论与实践,上海环境科学,2003,22(11):785~789
    [28] 上海市环境科学院,《世界银行——上海城市交通项目:减少上海城市车辆排污危害的战略》,1997.9
    [29] 上海市机车污染综合防治领导小组办公室,《上海市机动车污染综合防治规划及规划纲要》,2000,3
    [30] 上海市公安局车辆管理所.机动车统计报表.1990~2002.
    [31] 王立柱,隋强等,济南市机动车排放因子的确定,交通环保,2002,23(2):18~20
    [32] 吴必君,李利新,王伟 基于GIS城市机动车尾气扩散迁移研究.环境污染与防治,2002,24(4):240~242
    [33] 谢邵东,张远航,唐孝炎。我国城市地区机动车污染现状与趋势,环境科学研究,2000,13(4):22~25
    [34] 杨建军,郑庆玲,城市交通路口空气污染对人体健康的影响及防治措施,山东环境,1997,(3):13~14
    [35] 杨边日,上海带着环境忧虑进入私人汽车时代,世界环境,1998,(4):44
    [36] 张超,陈丙咸,邬伦 地理信息系统[M] 北京:高等教育出版社,1995
    [37] 张凌东,柯智明,汽车排气污染与防治,城市环境,2002,16(3),:40~42
    [38] 周淑珍,束炯,城市气候学,气象出版社,1994年8月
    [39] 祝昌健,广州市机动车尾气排放系数及污染趋势探讨,中国环境科学,1997,17(3):216~219
    [40] A.K.Luhar and R.S.Patil.1989.A general finite line source model for vehicular pollution prediction. Atmospheric Environment, 23:555-562
    [41] Amparo Moragues, Teresa Alcaide, The use of a geographical information system to assess the effect of traffic pollution, The Science of the Total Environment 189/190 (1996) 267-273
    [42] Andrew U. Frank, Irene Campari. 《Spatial Information Theory: a theoretical basis for GIS》.Berlin: Springer-Verlag,c1993
    [43] Assessment and Standards Division Office of Transportation and Air Quality, U.S. Environmental Protection Agency, User's Guide to MOBILE6.1 and MOBILE6.2: Mobile Source Emission Factor Model
    [44] Benson P.E. (1984) CALINE4 - A Dispersion Model for Predicting Air Pollutant
    
    Concentrations near Roadways. Federal Highway Administration Report FHWA/CA/IL - 84/15, California State Department of Transportation, Sacramento, California (NTIS PB 85 211498/AS)
    [45] CALINE4-A Dispersion Model For Predicting Air Pollutant Concentrations Near Roadways, Report NO. FHWA/CAA/TL-84/15, Revised June 1989
    [46] Cheung C S, Zhao Hui, Hung W T, Determination of Emission Factors of Motor Vehicles from On-Road Emissions Measurement, Transactions of CSICE, Vol.17(1999) No. 1:47~53
    [47] Gualtieri G, Tartaglia M. Predicting Urban Traffic Air Pollution: A GIS Framework. Transportation Research—Part D. Transport & Environment, 1998,13(5): 329~226
    [48] Helmut Mayer, Air pollution in cities, Atmospheric Environment 33(1999) 4029-4037)
    [49] Hey L E, Goodchild M F. Modeling the Effects of Clinmate Change on the Water Resources in the Gunnision River Basin, Colorado, Environmental Modeling with GIS [M]. Oxford University Press, 1993
    [50] Helmut Mayer, Air Pollution in cities, Atmospheric Environment 33(1999) 4029-4037
    [51] J.E.Moore. Geographic Information System Technology and its Application in Civil Engineering. Civil Engineering System, 1995,12:21~35
    [52] Johnson W.B. et al. An Urban Diffusion Simulation Model for Carbon Monoxide. Journal of Air Pollution Control Association, 1973,23(6):190~198
    [53] Manfred Seika, Roy M.Harrison, Norbert Metz, Ambient Background Model (ABM): Development of an Urban Gaussian Dispersion Model and ITS Application to London, Atmospheric Environment, 1998,Vol.32 No. 11:1881~1891
    [54] Matthias Schmidt, Ralf-Peter Schafer, An integrated simulation system for traffic induced air pollution, Environmental Modelling & Software 13 (1998) 295-303 )
    [55] Nokes W. and P. Benson (1985) Development of Worst Case Meteorology Criteria. Caltrans Report No. FHWA/CA/TL-85/14.
    [56] P.Goyal, T.V.B.P.S. Rama Krishna, A line source model for Delhi, Transportation Research Part D 4 (1999) 241-249.
    [57] Radian Corpporation Aiming at a moving target[M]. Controlling Mobile Sources in Mexico City, 1994.
    [58] R.Mclaren and D.L.Singleton. Analysis of Motor Vehicle Sources and Their Contribution to Ambient Hydrocarbon Distributions at Urban Sites in TORONTO During the Southern Ontario Oxidants Study. Atmosphere Environment, 30(12), 1996
    [59] Shu Jiong. Magnetic properties of daily sampled total suspended particulates in Shanghai. Environment Science and Technology, 2000,34:2393~2400.
    [60] Shu Jiong. Determing the sources of atmospheric particles in Shanghai China from magnetic and geochemical properties. Atmospheric Environment, 2001,
    
    (35~15):2615~2625.
    [61] Tony Held, Daniel P.Y. etc. UCD 2001:an improved model to simulate pollutant dispersion from roadways, Atmospheric Environment, 37(2003) 5325-5336
    [62] User's Guide for CL4: A User-friendly Interface for the Caline 4 Model for Transportation Project Impact Assessments, User's Guide STI-997480-1814-UG,June 20,1998
    [63] User's guide to MOBILE6.1 and MOBILE6.2: Mobile Source Emission Factor Model, United States Environmental Protection Agency, March 2002
    [64] Western Governor's Association Denver, Colorado and Binational Advisory Committee. Mobiel5-Mexico Documentation and User's Guide. Nov.20,2000
    [65] Turner, D.B. (1970) Workbook of Atmospheric Dispersion Estimates, Environmental Protection Agency.

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