ENERGY, ENVIRONMENT, ECOSYSTEMS, DEVELOPMENT and LANDSCAPE ARCHITECTURE Emissions of NOx and CO2 produced by the Mobile Military Vehicles in the Army of the Czech Republic HANA GAVENDOVA Civil Protection Department University of Defence Kounicova 65, 662 10 Brno CZECH REPUBLIC [email protected] whttp://www.vojenskaskola.cz Abstrakt: The paper deals with emissions that are produced by military vehicles in the Army of the Czech Republic. Emissions of nitrogen oxides and carbon dioxides are calculated from fuel consumption of mobile military vehicles and emission factors according to approved measurements. The monitoring of emission levels in the Army of the Czech Republic is estimated at the present time and the described method put more precisely estimation of the total emissions originating from mobile pollution sources in the Czech Republic. Key-Words: Emissions, Emission Factors, Military Vehicles, European Emission Standard, Fuel Consumption. - System for Monitoring of Atmospheric Deposition, - Register of Emissions and Air Pollution sources. As above mentioned, one of the tools of air protection by the state is Register of Emissions and Air Pollution sources [3]. Register among others contain so-called “other mobile sources”, but the emission level from this vehicles is till now only estimated. The followed chapters described way, how to put precisely estimation of emissions of chosen pollutants originating from mobile military vehicles. 1 Introduction Army of the Czech Republic, together with the other sectors, is concerned in emission balance of mobile sources, especially by the special military vehicles. The Czech Army integrated the air not only by the “classical” vehicles, that are also used in the civil sector such as passenger cars, lorry transport etc, but also “special” military vehicles typical for every army, such as tanks, infantry fighting vehicles, armored personnel carriers etc. Vehicles have been powered by internal combustion engines which operate on fossil fuels, e.g. gasoline and diesel. The combustion process produces CO2 and H2O as the main products. Unfortunately, combustion also produces several by-products which either originates from incomplete fuel oxidation – CO, particulate matter - or from the oxidation of noncombustible species present in the combustion chamber – NOx [1]. The pollution entails a lot of negative effects causing environmental and human risks and that is the monitoring is necessary. The monitoring and measurement of pollutants is steadily developing and leading up to superior data for air quality assessment [2]. 2.1 Register of Emissions and Air Pollution sources For the purpose of air quality monitoring is used REZZO – Register of Emissions and Air Pollution sources. Pursuant to the legislation (Lw No. 86/2001) which came into force in 2002 air pollution sources are divided into several categories to carry out emission inventories [4]. Complying with this categorization, the Air Quality Information System (ISKO) operated by CHMI (Czech Hydrometeorological Institute) includes REZZO database which serve for archiving and presenting data on stationary and mobile air pollution sources. The REZZO serves for the national emission inventory and the emission sources are divided into four categories (table 1) for which individual REZZO 1-4 databases have been introduced [5]. Extra large, large and medium-sized air pollution sources are monitored individually as point sources, small sources at regional and local level as area sources and mobile sources as line sources (road 2 Emissions Monitoring For the purpose of air quality monitoring, the following tools are used in the Czech Republic: - Emission level account from the air pollution source, - Imission Monitoring Stations, ISSN: 1790-5095 263 ISBN: 978-960-474-125-0 ENERGY, ENVIRONMENT, ECOSYSTEMS, DEVELOPMENT and LANDSCAPE ARCHITECTURE transport in sections controlled by vehicle census) and as area sources at regional level (other mobile sources) [6], [7]. Inventories of emissions from mobile sources are processed by the Transport Research Centre (CDV) Brno (road and other transport) and VÚZT Prague (agricultural and forestry vehicles) based on the reported statistical data (Czech Statistical Office) and the respective emission factors [8]. Information on emissions of pollutants obtained from REZZO 4 sources include road, railway, inland water and air transport and, since 1996, also information on emissions from mobile sources of agricultural and forest machinery prepared by VÚZT in Prague [9], [10]. The emission balance of so-called other mobile sources containing building machine, internal transport and military vehicles are only estimated [11]. From the time of commencement REZZO is completed by sources categories and the groups are more detailed. The significant changes have passed in declaration of basic pollutants. First, the solids pollutants, SO2, NOx, CO, VOC, NH3 were monitored. In the present time, further pollutants such as heavy metals, persistent organic substances and specific fraction of solids pollutants (PM10 and PM2,5) are monitored [12]. Till now, the emissions from military vehicles are not monitored, and thank to the suggested method is possible to calculate the emission level. Tab. 1: Sources according to the Register of Emissions and Air Pollution sources Source type stationary source mobile source Pollution Source Type extra large sources - REZZO 1 large sources - REZZO 1 medium-sized sources - REZZO 2 small sources - REZZO 3 mobile sources - REZZO 4 2.2 Methodology MESED and emission standards point point point surface line 50 MW and higher 5 – 50 MW 0,2 – 5 MW less than 0,2 MW - Method of recording individually collectively emissions of new vehicles that are sold in EU member states. The EES are defined in a series of European Union directives staging the progressive introduction of increasingly stringent standards. The competent and regulation organ in the area of emission regulation is Motor Vehicle Emission Group (MVEG). MVEG is a working group under the auspices of the European Commission, DirectorateGeneral Enterprise Unit Automobile Industry. The objectives of the MVED are especially completing, adapting and simplifying the Internal Market regulatory framework, promoting globalization of the technical regulatory framework through the United Nation [14]. The regulations are labeled EURO + the number of revision. The EURO 1 – EURO 6 mentioned emission limits for given type of vehicles. The EES regulate emissions of nitrogen oxide (NOx), hydrocarbons (HC), carbon monoxide (CO) and particulate matter (PM) for most vehicle type, including cars, lorries, trains, tractors and similar machinery, but excluding seagoing ships and airplanes. [15]. European The method works with categories and emission factors from the methodology MESED (Methodology of determination of air polluting emissions from transport). MESED was elaborated by Transport research Centre in Brno and it is used for calculation of regional and local emission level in the Czech Republic [13]. For distribution of the vehicles into categories are used these criteria: - accomplishment of EURO standard, - vehicles type, - used fuel. After 1992, Euro-related standards became mandatory in all European member states and a new type-approval test was introduces: EURO1-Euro6. At the present time, the EURO5 is valid. The time schedule of European Emission standard and year when they came or will come into force is described for passenger cars, commercial vehicles, lorries and buses in table 2. The European Union defines in European emission standards (EES) the acceptable limits for exhaust ISSN: 1790-5095 Heat input/output 264 ISBN: 978-960-474-125-0 ENERGY, ENVIRONMENT, ECOSYSTEMS, DEVELOPMENT and LANDSCAPE ARCHITECTURE Table 2: Time schedule of European Emission Standard EURO Regulation EURO 1 EURO 2 EURO 3 EURO 4 EURO 5 EURO 6 Passenger cars 1992 (1.7.) 1996 2000 2005 Commercial vehicles 1994 1998 2002 2006 2009 (1.9.) 2014 (1.9.) The methodology MESED is based on distribution of vehicles into 17 categories, for the Army of the Czech Republic, are relevant 12 of them (table 3). The categories have attached emission factors according to available measurements and are put in g.kg-1 of fuel. The emission factors are reviewed with a help of special tests at most used Czech and foreign cars. Lorries and buses 1992 1996 2000 2005 In the table 3 there are described categories of the military vehicles and their labeling. Every category contains emission factor of CO, NOX, CO2 and other pollutants according to available measurement. The emission factors for chosen pollutants are contented in the table 2. Emission factors are put in g.kg-1 of fuel. The emissions factors are reviewed with a help of special tests at the most used Czech and foreign cars. Table 3: Emissions factors for chosen pollutants No. Labeling 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. A B11 B12 B13 B21 B22 B23 C11 C12 C13 D11 D12 Description of category Motorcyclist Petrol passenger and light duty vehicles, conventional Petrol passenger and light duty vehicles, EURO 1 or EURO 2 Petrol passenger and light duty vehicles, EURO 3 and higher Diesel passenger and light duty vehicles, conventional Diesel passenger and light duty vehicles, EURO 1 or EURO 2 Diesel passenger and light duty vehicles, EURO 3 and higher Diesel heavy duty vehicles, conventional or EURO 0 Diesel heavy duty vehicles, EURO 1 or EURO 2 Diesel heavy duty vehicles, EURO 3 and higher Buses EURO 2 a older Buses EURO 3 a newer 3 Emissions of NOx and CO2 from Czech Army Vehicles s k. In the Army of the Czech Republic there is the computation of fuel computation monitored with the help of Logistics Informational System (LIS) which serves for planning of operations, maintenance and repairs of vehicles. Thank to LIS is possible to monitored the fuel consumption of every vehicle and eventually for every category. The total emissions are calculated according to formula 1. E z 12 s k 1 ISSN: 1790-5095 k . b .Ef z k k ρb Efzk Ez Emission f actors [g.kg - 1 ] NOx CO2 36,89 3183 45,09 3183 3,21 3183 1,07 3183 18,24 3183 8,49 3138 4,25 3138 93,39 3138 18,47 3138 10,26 3138 35,41 3138 11,34 3138 Fuel consumption for vehicle of the category k [dm3], Number of categories of military vehicles, Fuel density b [g.dm-3], Emission factor for chosen pollutant z [g.kg-1], Total emission pollutant z from chosen military vehicles [g.rok-1]. Whereas b, k Є N, where N is the symbol for the set of natural numbers and s,ρ < 0;∞) [2]. (1) 265 ISBN: 978-960-474-125-0 ENERGY, ENVIRONMENT, ECOSYSTEMS, DEVELOPMENT and LANDSCAPE ARCHITECTURE 3.1 Calculation of fuel consumption Total According to the formula (1) were acquired the total emissions. First, the calculation of fuel consumption for year 2005, 2006 and 2007 was performed. The values are illustrated in the table 4. From the table 4 is it evident that the largest fuel consumption was in year 2007, concretely 9,4.103 tone of fuel. The most high consumption was in categories B21 - Diesel passenger and light duty vehicles, conventional and C11 - Diesel heavy duty vehicles, conventional or EURO 0. 274,7 300,1 From the table 5 it is apparent that maximum emission of carbon monoxide was in year 2007. For all periods, the largest quantity of CO was produced by category C11 - Diesel heavy duty vehicles, conventional or EURO 0. It is the category where the highest emission factor for pollutant CO is. 3.3 Emissions of CO2 Further, from the fuel computation were calculated total emissions of CO2. In the table 6, there are the total emissions for every category and the total emissions for year 2005, 2006 and 2007. Table 4: Fuel consumption for categories of vehicles in particulate years Fuel consumption in particulate years [t] Cat. 2006 2007 2 007 A 10,3 52,9 11,0 B11 425,4 494,2 30,8 B12 836,1 641,9 581,1 B13 589,6 754,0 947,7 B21 1289,4 1336,5 2192,7 B22 565,9 442,8 339,4 B23 414,7 963,7 1113,9 C11 1775,7 1949,2 2108,8 C12 423,1 480,4 487,5 C13 709,4 755,6 660,8 D11 737,6 425,4 559,7 D12 131,6 121,4 105,8 Total 7908,8 8417,9 9409,9 Table 6: Total emission of carbon dioxide Emissions of CO2 in chosen years [t] Cat. 2005 2 006 2 007 A 33 168 35 B11 1 517 1 572 1 075 B12 2 91 2 043 2 071 B13 2 458 2 400 3 378 B21 4 104 4 254 6 979 B22 1 801 1 409 1 080 B23 2 350 3 024 3 495 C11 5 660 6 214 6 722 C12 1 348 1 531 1 553 C13 2 226 2 370 2 073 D11 2 314 1 334 1 756 D12 413 381 331 Total 24515 26700 30548 The maximum emissions of CO2 was in year 2007 and the largest quantity of CO2 was produced by category B21 Diesel passenger and light duty vehicles, conventional and the second highest were emission of CO2 in category C11 - Diesel heavy duty vehicles, conventional or EURO 0 in year 2007. The maximum emissions of CO2 in year 2005 and 2006 were in category C11 - Diesel heavy duty vehicles, conventional or EURO 0. They are the categories where the highest emissions factors for pollutant CO and the highest fuel consumption are. 3.2 Emissions of NOx From the fuel computation were calculated total emissions of NOx for every category of military vehicles. In the table 5, there are the total emissions for every category and the total emissions for year 2005, 2006 and 2007. Table 5: Total emission of nitrogen oxide Emission of NOx in chosen years [t] Cat. 2005 2 006 2 007 A 0,4 2 0,4 B11 21,5 22,3 15,2 B12 3 2,1 2,1 B13 0,8 0,8 1,1 B21 23,5 24,4 40 B22 4,8 3,8 2,9 B23 1,8 4,1 4,7 C11 165,8 182 196,9 C12 7,8 8,9 9 C13 7,3 7,8 6,8 D11 26,1 15,1 19,8 D12 1,5 1,4 1,2 ISSN: 1790-5095 264,3 4 Conclusions On the ground of continually increasing amount pollutant presenting in the air, it is necessary to solve problems of air pollution also for the sources which are not monitored at the present time. Among these sources belong military vehicles especially vehicles such as tank, infantry fighting vehicles or armored personnel carriers. 266 ISBN: 978-960-474-125-0 ENERGY, ENVIRONMENT, ECOSYSTEMS, DEVELOPMENT and LANDSCAPE ARCHITECTURE For the calculation of emission level were used emission factors according to the MESED methodology developed by Transport Research Centre in Brno and data from Information Logistic System, where the fuel computation monitored is. In the paper there was presented method for the calculation of emissions of chosen pollutants - NOx and CO2 - that serves for Register of Emissions and Air Pollution sources, mobile sources REZZO 4. The calculation emission of military vehicles, so-called “other mobile sources”, put more precisely estimation of the total emissions produced Czech Army that were up to this day only estimated. References: [1] EMEP/CORINAIR – Emission Inventory Guidebook. Environment Agency, 2007. [2] [3] <http://www.env.cz/cz/ znecisteni_ovzdusi_dopravy>. Environment in CR: Air. WWW:< http: www.envir.ee>. [10] Transport research Centre. Výzkum zátěže životního prostředí z dopravy. Brno : CDV, 2006. [11] Adamec, V. Safety risks of transport, possibilities for reducing of consequences and prevention. Ostrava: VŠB – Technical University in Ostrava, 2007, p. 233. [12] MACHÁLEK, P. Emisní inventury a podíl dopravy na znečišťování ovzduší. In II. Konference Doprava, zdraví a životní prostředí. Brno : CDV, 2006. 27- 31 s. ISBN 80-86502-33-3. [13] Dufek, J., Huzlík, J., Adamec, V. Methodology of determination of air polluting emissions from transport in the Czech Republic. CDV, Brno. 2002. p. 22. Motor Vehicle Emission Group. WWW: <http:ec.europa.eu>. Atmospheric European Gavendova, H., Pear, G. CH. Carbon monoxide from the vehicles used in the Army of the Czech Republic. In Energy Problems and Environmental Engineering,WWAI´08. WSEAS, 2008, pp. 471-475. ISBN978-960474-093-2, ISSN 1790-5095. [14] Gavendova, H., Bumbova A. Emission from the Military Vehicles. In Lecture Notes on Energy and Environment. WWAI´07. WSEAS, 2007, pp. 244-247. ISBN 978-960-6766-09-1. ISSN 1790-5095. [4] Ministry of Environment. Law No. 86/2001 Col. about Air. Prague, 2001. [5] IHEAL. REZZO – Register of Emissions and Air Pollution Sources. http:www.ecn.cz/rtk/gis/rezzo_le/rezzo_info.ht m. [6] Czech Hydrometeorological Institute - Air Quality Protection Division. Air pollution in the Czech Republic in 2007. WWW: <http://frailea.chmi.cz/ uoco/isko/groce/gr07e/akap1.html>. [7] MACHÁLEK, P. Emission and Sources Section. WWW: <http://frailea. chmi.cz/uoco/odd/oez_idxe.html>. [8] Ministry of Environment. Pollution from transport - Znečištění ovzduší z dopravy [online]. [cit. 2009-04-20]. WWW: ISSN: 1790-5095 [9] [15] 267 European emission standards.WWW http: <en.wikipedia.org>. ISBN: 978-960-474-125-0
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