Sonstige
Filtern
Dokumenttyp
- Buch (Monographie) (3) (entfernen)
Sprache
- Englisch (3) (entfernen)
Schlagworte
- Test (3) (entfernen)
Institut
- Sonstige (3) (entfernen)
High demands on exhaust emissions of passenger cars and light commercial vehicles require complex technologies. The three-way catalytic converter is an essential part of state of the art emission control systems. If a catalytic converter is damaged or its effectiveness deteriorates, it can be replaced by a replacement converter. Replacement catalytic converters from the aftermarket are approved on the basis of Regulation No 103 of the UNECE - United Nations Economic Commission for Europe. According to this regulation the replacement catalytic converter shall be designed, constructed and capable of being mounted so as to enable the vehicle to comply with the provisions taken as a basis for its type approval. Furthermore the pollution emissions must be effectively limited throughout the entire normal service life of the vehicle under normal operating conditions. In the context of the research project, the durability of replacement catalytic converters was examined. A VW Golf with emission standard Euro 4, 1.4 l petrol engine (55 kW) was selected as a test vehicle. At the start of the examinations, the vehicle showed a mileage of 75,000 km. The selected vehicle was regularly serviced in accordance with the manufacturer's specifications. No emission-relevant faults were recorded by the OBD system. The initial control measurement of the vehicle in as-delivered condition with the originally installed catalytic converter showed that the corresponding emissions of the regulated pollutants were considerably below the Euro 4 emission limits to be applied. Subsequently, an original replacement catalytic converter, which was purchased from an authorised dealer, and 4 catalytic converters purchased in the independent aftermarket, were examined. The replacement catalytic converters were conditioned according to the specifications of ECE Regulation No 103 and then measured in new condition. The catalytic converters were then aged on a burner test rig. Here a total mileage of 80,000 km was simulated. After 10,000 km and 40,000 km, the ageing was interrupted and the exhaust gas emissions of the test vehicle with the aged catalytic converters were measured. The examination was ended as soon as a limit value had been exceeded. The results of the project indicate that with the replacement systems for the after-treatment of exhaust gases available in the independent aftermarket, considerable quality differences can occur. At the end of the ageing over a distance of 80,000 km only the original replacement catalytic converter and one replacement catalytic converter from the independent aftermarket complied with the Euro 4 emission limits. With one replacement catalytic converter, the Euro 4 emission limits were already exceeded in new condition. With another replacement catalytic converter, the examination was aborted after 10,000 km ageing and with a further catalytic converter after 40,000 km ageing due to the Euro 4 emission limits being exceeded. The ECE Regulation No 103 provides for a test of durability of such systems over 80,000 km, but also alternatively enables the use of fixed deterioration factors. In practice, the durability of the replacement systems for the after-treatment of exhaust gases is guaranteed by their manufacturers. However, replacement catalytic converters are rarely inspected as part of the approval. In-use compliance provisions for replacement systems for the after-treatment of exhaust gases are not mentioned in the corresponding specifications. The results of this study indicate that the requirements in the ECE Regulation No 103 are not adequate to ensure the durability of replacement catalytic converters.
Mobility plays an important role in the Federal Republic of Germany. Motorised private transport and, consequently, passenger vehicles are the crucial factor. Vehicles should be environmentally and socially compatible yet also economically efficient at the same time. The crucial factor for pollution of the environment from road traffic is the exhaust emissions of the vehicles on the road. This is why, with the Directive 98/69/EC and the related introduction of exhaust emission standard Euro 3, the testing of the conformity of passenger and light commercial vehicles (in-service conformity check) was introduced. Vehicles already on the roads are to be examined again under type examination conditions (Type I Test) after a statistical selection process. In this way it is to be ensured that the systems and components relevant for the exhaust emissions of a vehicle will also function after several thousand kilometres. This is why the vehicles are checked again during in-service conformity check with respect to their limited pollution components. Due to the ever greater significance of CO2 emissions, both the CO2 emissions and the fuel consumption were included in this research project. For the success of such a project the choice of vehicle is of critical importance. Since this is the only way it is possible to also obtain a representative result. Therefore, in addition to the selection criteria required by law, statistical and technical criteria are also considered. The vehicle owners were selected on a random basis. All test vehicles were checked with respect to their pollutant components in the emissions laboratory in accordance with their standard. By law the same testing conditions apply in an in-service conformity check as in the relevant type approval. In this research project a total of 17 vehicle types were examined. Six types were equipped with positive-ignition engines and 11 types with compression ignition engines. Both groups were to each include vehicles of the limits Euro 4 and Euro 5. For vehicle types with positive-ignition engines, there was one type with the exhaust emission standard Euro 5. All others satisfied the exhaust emission standard Euro 4. For the vehicle types with compression ignition engines, 4 types satisfied exhaust emission standard Euro 5 and 7 types fulfilled exhaust emission standard Euro 4. Among the vehicle types with compression ignition and exhaust emission standard Euro4, there were 4 types of category M1 and 3 types of category N1 of class III. The aim of the research project is to examine the exhaust emissions in-service conformity of passenger and light commercial vehicles in operation to draw conclusions concerning the durability of engine components and systems for exhaust emission treatment. Overall in this in-service conformity testing programme, we were able, in accordance with the statistical procedure, to assess all 17 of the vehicle types tested as "positive". With the exception of one vehicle type, it was possible to conclude the random test for all vehicle types tested with the minimum random sample. This means that all 3 vehicles of one type in as-delivered condition complied with or fell below the respective limits for pollutant emissions according to the criteria of the statistical procedure. In the case of one vehicle type, where the random sample had to be enlarged, it was necessary to examine a total of 8 vehicles. Furthermore, with all vehicle types the CO2-emissions and fuel consumption (Type I Test) were determined to subsequently compare the measured CO2 emissions with those of the manufacturers. Of the 17 vehicle types examined, eleven vehicle types complied with the relevant manufacturers" values or fell below them. With six vehicle types, the CO2 emissions were more than the permissible 4% above the manufacturer- value during the Type I Test.
Although the bus belongs to the safest traffic means, single accidents can be particularly severe and concern many passengers. Especially in case of fires a high number of injured and killed persons can be the outcome. Fire safety of buses therefore is of high importance. With the increase of plastic materials as a material for the interior equipment of buses and coaches due to their good mechanical properties combined with low weight, the question arises whether the safety level has decreased in case of a fire during the last years " also compared to other means of transport. Because of the combustible plastics and their ability to release a high amount of heat the main fire load in buses is no longer the fuel but the plastic materials which are also often easy to ignite. Besides the flammability of the equipments, also the production of smoke, the smoke development and propagation as well as its toxicity are of interest. That counts for the passengers as well as for the test methods and its limit values. The severe fire in Germany near Hanover in 2008 with 20 fatalities showed how disastrous such fires can be. For those reasons several research projects were initiated on behalf of the German Federal Highway Research Institute. At the one hand the fire behaviour of coach interiors was examined in general focusing on fire propagation as well as fire detection and signalling. As result, recommendations with regard to early fire detection systems for the engine compartments and onboard extinguishing equipment were elaborated. On the other hand research was carried out to examine heat release, smoke, smoke propagation and its toxicity due to burning bus interior materials. In this project small and real scale experiments on material specimens, interior parts and vehicles were performed. Trains and buses often have very similar operation conditions. Consequently, bus interior material was tested according to the regulations for rail vehicles, i.e. DIN EN 45545 as well as DIN 5510. None of the tested bus interior materials would have been allowed to use in a train. The fire safety regulations for bus materials are on a low level compared to other transport sectors, i.e. railway, ship and aircraft. Also numerical investigations with the Fire Dynamics Simulator (FDS) were performed. The very rapid fire development during the severe bus fire from 2008 could be predicted with the numerical model. The model was then used to investigate the influence of different materials, ventilation conditions and ignition sources. The bus materials contribute significantly to a very rapid fire development in bus fires. Especially, the flammable ceiling and the passenger seats were identified to be key issues of the fire propagation in a bus and can be explained by the rapid fire spread along the ceiling and the high fire load of passenger seats. As conclusion of the project effective and economically reasonable fire safety requirements for interiors of buses are recommended which would improve the current situation. Proposals for amendments of current requirements are recommended including the specification of appropriate limit values. In particular, it is taken into consideration which reasonable fire safety standards from other transport sectors, especially the rail sector, should be transferred to buses