High-efficiency phosphorescent organic light emitting diodes using TCTA-TAZ as a double host and Ir(ppy)3 as a dopant were fabricated and their electro-luminescence properties were evaluated. The fabricated devices have the multi-layered organic structure of 2-TNATA/NPB/(TCTA-TAZ) : Ir(ppy)3/BCP/SFC137 between an anode of ITO and a cathode of LiF/AL. In the device structure, 2-TNATA[4,4',4"-tris(2-naphthylphenyl-phenylamino)-triphenylamine] and NPB[N,N'-bis(1-naphthyl)-N,N'-diphenyl-1,1'-biphenyl-4,4'-diamine] were used as a hole injection layer and a hole transport layer, respectively. BCP [2,9-dimethyl-4,7-diphenyl-1,10-phenanthroline] was introduced as a hole blocking layer and an electron transport layer, respectively. TCTA [4,4',4"-tris(N-carbazolyl)-triphenylamine] and TAZ [3-phenyl-4-(1-naphthyl)-5-phenyl-1,2,4-triazole] were sequentially deposited, forming a double host doped with Ir(ppy)3 in the [TCTA-TAZ] : Ir(ppy)3 region. Among devices with different thickness combinations of TCTA (50 Å-200 Å) and TAZ (100 Å-250 Å) within the confines of the total host thickness of 300 Å and an Ir(ppy)3-doping concentration of 7%, the best electroluminescence characteristics were obtained in a device with 100 Å-think TCTA and 200 Å-thick TAZ. The Ir(ppy)3 concentration in the doping range of 4%-10% in devices with an emissive layer of [TCTA (100 Å)-TAZ (200 Å)] : Ir(ppy)3 gave rise to little difference in the luminance and current efficiency.

To investigate characterization of EMF(Electromagnetic Field) emission from VDT(Visual Display Terminal) in computer room, we were divided into 3 types of placement monitors which are 1) back side of monitor faced the ground(back view type), 2) arrangement of monitors was a line type(two sides type), and 3) disposition of monitors was s straight(horizontal line type). We also measured monitors classified types at the front, side and back by distance and evaluated by TCO(The Swedish Confederation of profession Employers) and MPR-2(Measure and Proof Radiation Board) guide line. Magnetic field emission level by the type of VDT, it was indicated that MF(Magnetic Field) level was below the backgrounds level when CRT moved away about 70~90cm, LCD moved away about 40~50cm. We evaluated MF emission level by the number of VDT, it did not show any relationship. Finally, estimated MF emission level by the placement of VDT, it was showed the MF level less than the background level, when VDT moved away 40~50cm in all dispositions with exception of 2 sites. Background level of case was higher than emitted from VDT, so that did not effect on MF level by distance. However, we find out that as distance increased, MF emission level decreased significantly in all cases. We measured MF emission level of one monitor and others (back and forth) monitor in line type. Below the background level when one monitor type moved away 70cm, others monitor type moved away 40cm. However, other monitor types affected MF level which is located back monitor. The data demonstrate that avoiding excessive MF exposure from VDT using computer room, to have a space between user and VDT at least 50㎝.

This study characterized PM and VOC emissions from cow dung combustion in a controlled experiment. Dung from grass-fed cows was dried and combusted using a dual cone calorimeter. Heat fluxes of 10, 25, and 50 kW/m² were applied. The concentrations of PM and VOCs were determined using a dust spectrometer and gas chromatography/mass spectrometry, respectively. PM and VOC emission factors were much higher for the lower heat flux, implying a fire ignition stage. When the heat flux was 50 kW/m², the CO₂ emission factor was highest and the PM and VOC emission factors were lowest. Particle concentrations were highest in the 0.23-0.3-μm size range at heat fluxes of 25 kW/m² and 50 kW/m². Various toxic VOCs including acetone, methyl ethyl ketone, benzene, and toluene were detected at high concentrations. Although PM and VOC emission factors at 50 kW/m² were lower, they were high enough to cause extremely high indoor air pollution. The characteristics of PM and VOC emissions from cow dung combustion indicated potential health effects of indoor air pollution in developing countries.

This study investigated the characteristics of selected volatile organic compounds(VOCs) in newly-finished residential buildings, before the occupants moved in. This investigation was carried out by measuring the indoor and outdoor concentrations of selected VOCs before the occupants moved in and by utilizing an indoor mass balance model. Among 25 target VOCs, five aromatics(benzene, ethyl benzene, toluene, m,p-xylene, and o-xylene) were detected in all samples of both indoor and outdoor air. Toluene was most abundant VOC in the indoor air of new apartments, with a median value of 168 mg m-3. Unlike other VOCs, halogenated compounds would not be significantly emitted from building materials. The indoor air concentrations of all selected VOCs, except for 1,3,5-trimethyl benzene, exhibited significant correlations each other, while for outdoor air concentrations, five aromatics only were significantly correlated between them. The emission rate of toluene was higher for the current study(median value, 76.8 mg m-2 h-1) than for a previous study, while the emission rates of limonene, a-pinene and b-pinene(geometric means of 2.4, 13.8 and 9.6 mg m-2 h-1, respectively) were lower and the emission rates of m,p-xylene and 2-butanone(geometric means of 10.9 and 21.3 mg m-2 h-1, respectively) were similar. Although there were a few exceptions, the emission strengths are likely proportional to indoor temperature, and appear to reversely proportional to air exchange rate.

The emissions characteristics of particulate matters(PM) according to the types of wastes from industrial waste incinerator of 800 kg/hr treatment capacity were investigated. For this study, the incinerate waste are as follows; waste resin, waste wood, waste urethane, waste gunny, and waste paper. The particulate samples were collected to be emitted in stack and air pollution control(both cyclone and bag filter). In stack, the concentrations of PM were in the range of 2.61 to 26.51 ㎎/S㎥ and the major chemical species were C, Si, Cl, K, Na, Ca in all the wastes. In cyclone fly ash, the mean content of heavy metal were in the order of Fe > Zn > Pb > Cu > Mn > Cr > Ni > Cd > As > Hg and the heavy metal content of waste resin were Zn 34,197.5 mg/kg, Fe 27,587.6 mg/kg, Pb 6,055.8 mg/kg, respectively. In bag filter fly ash, the mean content of heavy metal were in the order of Zn > Pb > Fe > Cu > Mn > Cd > Cr > Ni > As > Hg and the heavy metal content of waste wood were Pb 36,405.2 mg/kg, Fe 15,762.9 mg/kg, Cu 9,989.5 mg/kg, Cd 2,230.1 mg/kg, respectively. Comparing the heavy metal content of both cyclone and bag filter, in cyclone, the Cr, Fe, Ni content were higher than in bag filter and the Cd, Cu, Hg content were lower than in bag filter.