The manufacturing of catalyst and novel material was performed to enhance the reaction rate of a process and to be used as solid sorbent for certain gas. The area is divided into several different programs:
Catalyst Synthesis for Thermochemical Process
Novel Material for biogas purification at Low and High Temperatures
The application of the various promising types of solid chemisorbents for biogas purification and other application is still in the fundamental research stage. Therefore, a systematic study targeting their performance enhancement is crucial, since they have the potential to make industrial biogas purification processes economical, mitigate the GHG effects of greenhouse gases, and secure the environment's well-being. Towards this end, various gaps in the literature and fundamental ideas will be addressed, in order to create novel, cost-effective and high-performing solid sorbents with very low environmental impact.
The performance of a chemical-looping process (combustion, reforming, gasification) heavily depends on the efficiency of the material that will be used as an oxygen carrier. In order to develop a highly efficient, cost-effective oxygen carrier, preliminary screening of materials and production conditions is needed. It is critical to find a range of material combinations that are suitable for the chemical-looping process in at certain temperature and pressure conditions. Different oxygen carriers' efficiencies and physicochemical behaviors must be evaluated and compared. Moreover, the effects of operating conditions, such as air-to-carrier ratio, oxygen-carrier-to-fuel ratio, fuel gas velocity and reactor temperature, on fuel conversion is also of significant importance.
Thermochemical conversion research divided into several different programs
Char Production Using Torrefaction
Bio-oil Production from Lignocellulosic Biomass
Catalytic Pyrolysis and Bio-oil Upgrading
Coal and Biomass Gasification
Torrefaction is a mild thermochemical process carried out in a temperature range of 200 0C to 300 0C in nitrogen atmosphere. During torrefaction the lignocellulose structures of biomass undergoes mainly in hemicellulose. Also, during torrefaction the OH groups in the biomass are destroyed and thus makes the biomass hydrophobic in nature and O/C ratio is reduced thereby increasing in carbon content and the resulting product resemble to that of a coal. The high fuel quality of torrefied biomass makes it very attractive for combustion and gasification applications. The torrefied biomass also finds it application as high quality smokeless fuel for industrial, commercial and domestic application, as a solid fuel for cofiring directly with pulverized coal at electric power plant and as an upgraded feedstock for fuel pellets, briquettes and other densified biomass fuels.
Among the thermochemical processes, pyrolysis is a promising tool for providing bio-oil that can be used as fuel or chemical feedstock. The pyrolysis of biomass is a very old energy technology that is again becoming attractive among various systems for the use of biomass as a source of energy. Pyrolysis is a thermochemical process carried out in the temperature range of 300 0C to 600 0C in inert atmosphere. Thermogravimetric analysis (TGA) is one of the most frequently used techniques to study the primary reactions of the decomposition of solids. In the case of biomass, thermogravimetric techniques have been used for the identification of different fractions of polymer present in the material. The kinetic study of biomass pyrolysis is of relevant importance because it constitutes the initial step of the combustion and gasification processes. Knowledge of the kinetics for the thermal decomposition of lignocellulosic materials is needed for the design of gasifier and pyrolysis reactors.
Lignocellulosic biomass can be converted to bio-oil using pyrolysis and then followed by catalytic upgrading of the bio-oil. Pyrolysis can be categorized into conventional pyrolysis (slow pyrolysis) and fast pyrolysis depending on the operating condition. In slow pyrolysis, biomass is heated to temperature up to 500 oC with heating rate less than 100 degree/minute and vapour residence time of 5-30 min, resulting mainly in char production. In fast pyrolysis, biomass is heated to temperature up to 500 oC, but with faster heating rate (1000 degree/minute and up) and vapour residence times less than 2 second. The second type of the pyrolysis naturally favours the bio-oil as the main product unlike the first type favours the solid product (bio-char).
There are several general chemical changes occurred during pyrolysis. Primary pyrolysis reaction releases volatiles and at the same time forms char. On the next step, condensation process can occurred in the cooler parts of the system to form bio-oil. This process naturally followed by secondary reactions that produce tar. Reforming, dehydration and polymerization can also occurred depend on the reaction time and the heating rate. In the end, the volatile pyrolysis product can have more than 120 components from unspecified low molecular product contained phenolic OH-groups to cyclic and bicyclic products.
Current and ongoing research in pyrolysis has been aimed to increase the yield of the bio-oil and at the same time to increase the quality of the oil by perform the upgrading process afterward. In this study, I propose a step for pre-treatment of the sample prior to the pyrolysis process in order to obtain a better quantity and quality of the bio-oil.
Nationally, the amount of waste sent to private and public waste disposal facilities in 2008 reached about 34 million tonnes in total. Overall, 26 million tonnes of that waste was disposed of in landfills or was incinerated and over 8 million tonnes was diverted or processed through material recovery facilities or centralized composting operations. Paper fibres, including newsprint, cardboard and mixed paper fibers, make up the largest portion of all diverted materials, accounting for 41%. There is a great potential to produce a value added product from non-residential sources while at the same reducing the amount of waste that end up in the landfill. The direct outcome of this research is: gaining a thorough understanding and evaluation of the challenges that are hindering the use of industrial waste to produce absorbent and ADC, understanding the general behavior of different material in the absorption process, producing high quality, cost effective, and environmentally friendly products.
Determining heating value of MSW and their suitability for producing value-added products
The goal of the program of "waste to value-added" initiative is to showcase the latest technologies that turn the municipal solid waste into value-added products in rural Malaysia. This project aims to gain a better understanding of the properties and variations of the locally available residential and ICI (industrial, commercial and institutional) MSW, especially the effects of water contents on their heating values for determining the threshold point during the pre-drying process for thermal treatment.
Although many studies about chemical reaction using TGA have been reported, the effects of important parameters such as particle size, heating rate and initial sample weight have rarely been investigated for several samples and process. In our study study, chemical process such as thermochemical conversion has been performed considering the effects of various parameters, such as particle size, sample initial weight and heating rate. The devolatilisation kinetics of the process has also been studied using nonlinear optimisation. Reaction kinetic parameters were obtained by considering the three different stages that occurred during pyrolysis. This research aims in investigating the chemical process characteristics and kinetics and the effect of several parameters on chemical process that are instrumental for scaling up the process.