The objective of this study was to investigate the effect of shoe dust on the indoor environment, and the effectiveness of shoe dust control on indoor air quality. Test dust was resuspended to reach a mass concentration of particles (2.5-10 μm size) more than 3 times compared to background level, and 1.5 times for particles less than 1 μm in size. The shoes, which were used for actual walking purposes in the outdoor environment, increased indoor PM10 concentration by 118±9%. The removal of shoe dust by water washing and mechanical suction brought about an improvement of indoor air quality. In particular, in circumstances where 27 people walked for one hour into the indoor environment, the mechanical suction of shoe dust decreased PM10 concentration by about 17% (based on the mass balance analysis).

The indoor level of phthalates in children-facilities was assessed in this study. The samples of house dust were collected at various children's facilities (40 day-care houses, 42 child-care centers, 44 kindergartens, and 42 indoor playgrounds) in summer (Jul~Sep, 2007) and winter (Jan~Feb, 2008) periods, and analyzed by GC-MS. The DEHP was detected in almost every sample (detection rate : 99%) and the detection rate of DnBP and BBzP was more than 80%. The average concentrations of DEHP, DEP, DnBP, and BBzP in house dust were 388 ㎍/g dust, 37㎍/g dust, 108㎍/g dust and 349㎍/g dust, respectively. The relationship between construction period and DEHP level was statistically significant. But, other factors such as flooring material, construction period and water leakage were not statistically significant relationship with phthalates levels. The Phthalate levels were similar or more higher than other the European country.

This study was followed up asthma incidence rate in primary schools indoor air quality. To investigate the history and prevalence rate of allergic diseases(asthma, atopy dermatitis, allergic rhinitis and conjunctivitis), the standardized and generally used International Study of Asthma and Allergies in Childhood(ISAAC) questionnaire was used to conduct the symptom survey for all participating subjects. The concentrations of major indoor air pollutants(dust mite allergen, aldehydes , VOCs, TBC, phthalate) were observed from April to May 2007. Sampling was undertaken at 19 primary schools. The sampling sites of air pollutants are classroom’s indoor and hallway. Dust mite allergen part it was detected from the case classroom and infirmary. The exposure quality of aldehyde and the place pollution level was indoor>outdoor>hallway, which whole is disease incidence rate high group appears more highly the low group than. The partially result of formaldehy and VOCs, the concentration of high environmental disease incidence rate showed also high. However, house dust allergen, TBC and phthalate measurement school was not the effect where the comparison of difference.

This study was performed to investigate airborne volatile organic compounds(VOCs), formaldehyde, respiratory particulate for concentration in primary schools. The concentrations of major indoor air pollutants(VOCs , benzene, toluene, ethylbenzene, xylene, styrene, formaldehyde, PM-10) were observed from November to December 2006. Sampling was undertaken at 81 primary schools. The sampling sites of air pollutants are classroom and hallway. VOCs with distribution of most of general environmental contamination material will be able to confirm that it shows the log-normal distribution which is similar exposure distribution. The exposure quality of VOCs and the place pollution level was indoor> hallway>outdoor, which whole is located in the metropolis and the industrial areas is higher than farm village area. It tried to observe the I/O ratio, it appeared highly from the interior of the material of most. The mean concentrations of formaldehyde, respiratory particulate were 22.07㎍/㎥, 88.06㎍/㎥ respectively. Indoor and outdoor ratios(I/O) of formaldehyde and respiratory particulate were 3.6 and 1.4, respectively. The concentration of respiratory particulate is 27.2% higher than guideline for school hygiene(100㎍/㎥). From the comparison in the construction year, the highest concentration of formaldehyde is showed under one year. However, as time passed by the concentrations of formaldehyde become lower.