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DESIGN,FABRICATION & PERFORMANCE STUDY OF A BATCH-TYPE FIXED-BED FIRE-TUBE HEATING PYROLYSIS SYSTEM FOR PRODUCTION OF LIQUID OIL FROM BICYCLY/RICKSHAW & TRUCK SCRAP TIRES

ABSTRACT


In this study a batch-type fixed-bed fire-tube heating pyrolysis system has been designed and fabricated to produce liquid oil from scrap tires. Waste materials in the form of bicycle/rickshaw and truck scrap tire were pyrolysed in an internally heated batch-type fixed-bed fire-tube heating reactor system. The solid waste tires in pieces form was pyrolyzed in a 10 cm diameter and 27cm height reactor. The feed sizes were 10cmxO.5cmxO.25cm to 25cmx2cmx0.25cm. The reactor was heated by means of uniformly distributed electric coils of total capacity 2800wt and LPG burner preheated the purging N2 gas. The products were oils, char and gas. The liquid and char products were collected separately while the gas was flared into atmosphere. The product liquid was collected in a series of ice-cooled liquid collector. The maximum liquid and char yield were 52% and 35% for bicycle/rickshaw tire and 60% and 23% for truck tire for feed size of 10cmxO.5cmxO.25cm and 10cmx2cmxlcm respectively. The condensed pyrolytic oils were analyzed for their physical properties. The fuel properties compared were physical properties and calorific value. The heat values of the liquids of truck tire and bicycle/rickshaw are 40733 kJ/Kg and 41000 respectively. The results of the analysis showed that the oils were favorable viscosity and high heat value. From this study it is found that the pyrolysis of solid tire wastes may be a potential source of liquid hydrocarbon fuels.

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EFFECT OF TEMPERATURE AND PRESSURE OF CHARCOAL ADSORPTION SYSTEM ON EMISSIONS WITH SPECIAL EMPHASIS ON EXHAUST ODOR IN A DI DIESEL ENGINE AT IDLING

ABSTRACT


Fuel consumption in petrol engines is about 20-30% higher than that of diesel engines that causes high CO2 emission as well as greater pollution of environment. DI diesel engines have the lowest fuel consumption as well as CO2 emissions. So, DI diesel engine vehicles are becoming popular day by day. But this increases both regulated and unregulated emissions like NOX, PM, exhaust odor and others. Among the various exhaust emission problems of DI diesel engine, odor is still a prominent exhaust emission problem. Reduction of exhaust odor can be done mainly in three ways. One of them is to optimize the engine parameters. But researches have shown that the reduction of odor is not significant. The other is that the use of alternative fuels. Some alternatives fuels can reduce the exhaust odor significantly but the cost is must higher than diesel fuel. The last one is exhaust gas after treatment. It is also of two types. One is to use the catalyst system. The catalyst system works only at high temperature condition i.e. when the vehicle is in running condition (under load). This system hence can not be applied at idling and at low temperature operation. The other is the non-catalytic system like adsorption type system, water washing system, air dilution system and others. Since the exhaust emission and odor at idling and low temperature operation is higher than any other engine condition and the exhaust gas temperature is much lower at idling and low speed operations, the charcoal adsorption system can be used. Some previous researches have showed that several organic compounds (aldehyde, organic acids and oxygenated compounds) are important odorous groups in exhaust and they correlate well with exhaust odor. Odor can be reduced greatly by adsorbing these odorous components by charcoal adsorption system. Last few years thesis report on odor reduction by charcoal-adsorption system showed that charcoal-adsorption system can reduce exhaust odor around 0.75 points. This thesis report focuses on the temperature and pressure effect of charcoal adsorption system. The experiment was performed first with a 1.5 ft long double chamber adsorption system and the odor is reduced about 0.25 points. It is clear that if a larger cold charcoal adsorption system (5 ft) is used the odor could be reduced far more, even more than 0.75 points. The double chamber adsorption system in which temperature was controlled can also reduce other emissions significantly. CO emissions also can be reduced with this system. Some combination of charcoal adsorption and air dilution systems were also used. These systems reduced odor level from 3.75 to 2.25. Other emissions (NOx, CO) are also significantly reduced.

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