The emission of odor, characterized by the combustion conditions and biomass types resulting from the use of a biomass incinerator, was analyzed. The following biomass types were considered: bark, board waste, sawdust, wood flour, wood fiver, wastewater sludge, and timber wastewater. As a study method, the physico-chemical characteristics of each biomass type were analyzed to predict the potential substances that might be emited under incomplete combustion conditions. And, the emission components of odor emission by biomass were analyzed at the laboratory level using a combustion device. In addition, the characteristics of the contaminant (odor) emission per mixture ratio of biomass were analyzed in a stoker incinerator that is in operation in an actual establishment at a scale of 300 ton/day. In the biomass emission experiment using the combustion device at the laboratory level, the major substances such as Acetic acid, Styrene, Toluene, Benzene, Dichloromethane, etc. were analyzed, and these components were determined to increase odor index. VOCs measurement in the outlet of the stoker incinerator indicated that Acetaldehyde, Ethanol, Acetonitrile, Ethyl acetate, Toluene, etc. were detected as the major substances. These were similar to the emission substances presented by the experiment that had investigated emissions by biomass type. A study on the Effect of Operational Conditions in biomass stocker incinerator on the concentration of odorous materials emitted from stack showed a close relationship between the input by biomass type and urea, temperature in the incinerator, and the tendency to emit/produce odor.

Cement production processes release various odor elements including acetaldehyde, hydrogen sulfide, formaldehyde and toluene etc. A three-dimensional numerical simulation using a commercial code of Computational Fluid Dynamics (CFD) was used to estimate the concentration profiles and dispersion distance around the local residential area. The calcination furnace, one of the main emission sources in the cement manufacturing process, discharged the odorous gases of H₂S, HCHO, CH₃CHO and C6H5CH₃at levels of up to 3.15 ppb, 5.1 ppm, 6.65 ppm and 0.74 ppm of H₂S, HCHO, CH₃CHO and C6H5CH₃respectively. This study found that as for the emission concentration of 1ppm for H₂S and CH₃CHO, the landing distance of the threshold value for each gas was extended in summer seasons at a low velocity. Low temperature of the flue gas at a high velocity also led to long dispersion.