1.Development of Physiologically Based Pharmacokinetic Model for Several Volatile Organic Compounds.
Jae Yeon JANG ; Kyung Jong LEE ; Ho Keun CHUNG
Korean Journal of Occupational and Environmental Medicine 1997;9(2):357-377
Recently physiologically based pharmacokinetic (PB-PK) model has important role in industrial and environmental health. One of problem in application of PB-PK models is that they have uncertainties that is due to different input parameters according to authors. In order to develope a PB-PK model that hag good validity, the effect of several input parameters on simulation results was studies. Chemicals studied were perchloroethylene, toluene and styrene. Simulation of alveolar concentration, blood concentration and urinary metabolites was performed for three solvents, respectively. Input parameters discusses were physiological parameters, metabolic parameters and partition coefficient of chemicals. By comparing simulation results according to several pairs of parameters with experimental data, input parameters that showed best fit were decided.
Environmental Health
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Solvents
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Styrene
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Tetrachloroethylene
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Toluene
;
Volatile Organic Compounds*
2.Quality Control of Residual Solvents in 18FFDG Preparations by Gas Chromatography.
Hak Jeong LEE ; Jae Min JEONG ; Yun Sang LEE ; Hyung Woo KIM ; Young Soo CHANG ; Dong Soo LEE ; June Key CHUNG ; Myung Chul LEE
Nuclear Medicine and Molecular Imaging 2007;41(6):566-569
PURPOSE: Analysis of volatile organic solvents in 2-deoxy-2-[18F] fluoro-D-glucose ([18F]FDG) preparations was performed by gas chromatography (GC), in accordance with USP. MATERIALS AND METHODS: Analyses were carried out on a Hewlett-Packard 6890 gas chromatography equipped with an FID. RESULTS: We determined the amounts of ethanol and acetonitrile on every batch of our routine [18F]FDG preparations, ranging between 5000 ppm and 100 ppm. In our routine preparation of [18F]FDG, the amount of acetonitrile and ethanol in the final product were well below the maximum allowable limit described in the USP. CONCLUSION: Our [18F]FDG preparations were in accordance with the suggested USP maximum allowable levels of the quality control analysis of volatile organic compounds.
Chromatography, Gas*
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Ethanol
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Quality Control*
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Solvents*
;
Volatile Organic Compounds
3.Modeling Human Exposure Levels to Airborne Volatile Organic Compounds by the Hebei Spirit Oil Spill.
Jong Ho KIM ; Byoung Kyu KWAK ; Mina HA ; Hae Kwan CHEONG ; Jongheop YI
Environmental Health and Toxicology 2012;27(1):e2012008-
OBJECTIVES: The goal was to model and quantify the atmospheric concentrations of volatile organic compounds (VOCs) as the result of the Hebei Spirit oil spill, and to predict whether the exposure levels were abnormally high or not. METHODS: We developed a model for calculating the airborne concentration of VOCs that are produced in an oil spill accident. The model was applied to a practical situation, namely the Hebei Spirit oil spill. The accuracy of the model was verified by comparing the results with previous observation data. The concentrations were compared with the currently used air quality standards. RESULTS: Evaporation was found to be 10- to 1,000-fold higher than the emissions produced from a surrounding industrial complex. The modeled concentrations for benzene failed to meet current labor environmental standards, and the concentration of benzene, toluene, ortho- meta- para-xylene were higher than the values specified by air quality standards and guideline values on the ocean. The concentrations of total VOCs were much higher than indoor environmental criteria for the entire Taean area for a few days. CONCLUSIONS: The extent of airborne exposure was clearly not the same as that for normal conditions.
Benzene
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Humans
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Petroleum Pollution
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Toluene
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Volatile Organic Compounds
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Volatilization
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Xylenes
4.Exposure Characteristics of Construction Painters to Organic Solvents.
Hyunhee PARK ; Hae Dong PARK ; Jae Kil JANG
Safety and Health at Work 2016;7(1):63-71
BACKGROUND: Construction painters have not been studied well in terms of their hazards exposure. The objective of this study was to evaluate the exposure levels of total volatile organic compounds (TVOCs) for painters in the construction industry. METHODS: Activity-specific personal air samplings were carried out in three waterproofing activities [polyurethane (PU), asphalt, and cement mortar] and three painting activities (epoxy, oil based, and water based) by using organic-vapor-monitor passive-sampling devices. Gas chromatograph with flame ionization detector could be used for identifying and quantifying individual organic chemicals. The levels of TVOCs, by summing up 15 targeted substances, were expressed in exposure-index (EI) values. RESULTS: As arithmetic means in the order of concentration levels, the EIs of TVOCs in waterproofing works were 10.77, 2.42, 1.78, 1.68, 0.47, 0.07, and none detected (ND) for indoor PU-primer task, outdoor PU-primer task, outdoor PU-resin task, indoor PU-resin task, asphalt-primer task, asphalt-adhesive task, and cement-mortar task, respectively. The highest EI for painting works was 5.61 for indoor epoxy-primer task, followed by indoor epoxy-resin task (2.03), outdoor oil-based-spray-paint task (1.65), outdoor water-based-paint task (0.66), and indoor oil-based-paint task (0.15). Assuming that the operations were carried out continuously for 8 hours without breaks and by using the arithmetic means of EIs for each of the 12 tasks in this study, 58.3% (7 out of 12) exceeded the exposure limit of 100% (EI > 1.0), while 8.3% (1 out of 12) was in 50-100% of exposure limit (0.5 > EI > 1.0), and 4 tasks out of 12 were located in less than 50% of the limit range (EI < 0.5). CONCLUSION: From this study, we recognized that construction painters are exposed to various solvents, including carcinogens and reproductive toxins, and the levels of TVOC concentration in many of the painting tasks exceeded the exposure limits. Construction workers need to be protected from chemical agents during their painting works by using personal protective devices and/or work practice measures. Additional studies should focus on the exposure assessment of other hazards for construction workers, in order to identify high-risk tasks and to improve hazardous work environments.
Carcinogens
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Construction Industry
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Flame Ionization
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Humans
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Organic Chemicals
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Paint
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Paintings
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Protective Devices
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Solvents*
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Volatile Organic Compounds
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Water
5.Effects of different field processing methods on volatile components of Chuanxiong Rhizoma: an exploration based on headspace gas chromatography-mass spectrometry.
Yi-Na TANG ; Jun-Xia GUO ; Qing-Miao LI ; Jin-Hai YI
China Journal of Chinese Materia Medica 2022;47(3):676-683
The volatile oil of Chuanxiong Rhizoma(CX) is known as an effective fraction. In order to seek a suitable method for processing CX and its decoction pieces, this study selected 16 volatile components as indices to investigate how different processing methods such as washing/without washing, sun-drying, baking, oven-drying and far-infrared drying at different temperatures affected the quality of CX and its decoction pieces(fresh CX was partially dried, cut into pieces, and then dried) by headspace gas chromatography-mass spectrometry(GC-MS), cluster analysis, principal component analysis and comprehensive weighted scoring. The results showed that the rapid washing before processing did not deteriorate the volatile components of CX. Considering the practical condition of production area, oven-drying was believed to be more suitable than sun-drying, baking, and far-infrared drying. The CX decoction pieces with a thickness of 0.3-0.4 cm were recommended to be oven-dried at 50 ℃. The integrated processing(partial drying, cutting into pieces, and drying) did not cause a significant loss of volatile components. For the fresh CX, the oven-drying at 60 ℃ is preferred. The temperature should not exceed 60 ℃, and drying below 60 ℃ will prolong the processing time, which will produce an unfavorable effect on volatile components. This study has provided the scientific evidence for field processing of CX, which is conducive to realizing the normalization and standardization of CX processing in the production area and stabilizing the quality of CX and its decoction pieces.
Desiccation
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Gas Chromatography-Mass Spectrometry/methods*
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Oils, Volatile
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Principal Component Analysis
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Rhizome/chemistry*
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Volatile Organic Compounds/analysis*
6.Exposure to Volatile Organic Compounds and Possibility of Exposure to By-product Volatile Organic Compounds in Photolithography Processes in Semiconductor Manufacturing Factories.
Seung Hyun PARK ; Jung Ah SHIN ; Hyun Hee PARK ; Gwang Yong YI ; Kwang Jae CHUNG ; Hae Dong PARK ; Kab Bae KIM ; In Seop LEE
Safety and Health at Work 2011;2(3):210-217
OBJECTIVES: The purpose of this study was to measure the concentration of volatile organic compound (VOC)s originated from the chemicals used and/or derived from the original parental chemicals in the photolithography processes of semiconductor manufacturing factories. METHODS: A total of four photolithography processes in 4 Fabs at three different semiconductor manufacturing factories in Korea were selected for this study. This study investigated the types of chemicals used and generated during the photolithography process of each Fab, and the concentration levels of VOCs for each Fab. RESULTS: A variety of organic compounds such as ketone, alcohol, and acetate compounds as well as aromatic compounds were used as solvents and developing agents in the processes. Also, the generation of by-products, such as toluene and phenol, was identified through a thermal decomposition experiment performed on a photoresist. The VOC concentration levels in the processes were lower than 5% of the threshold limit value (TLV)s. However, the air contaminated with chemical substances generated during the processes was re-circulated through the ventilation system, thereby affecting the airborne VOC concentrations in the photolithography processes. CONCLUSION: Tens of organic compounds were being used in the photolithography processes, though the types of chemical used varied with the factory. Also, by-products, such as aromatic compounds, could be generated during photoresist patterning by exposure to light. Although the airborne VOC concentrations resulting from the processes were lower than 5% of the TLVs, employees still could be exposed directly or indirectly to various types of VOCs.
Humans
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Korea
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Light
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Parents
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Phenol
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Semiconductors
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Solvents
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Toluene
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Transcutaneous Electric Nerve Stimulation
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Ventilation
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Volatile Organic Compounds
7.Health Risk Assessment and Analysis on the Volatile Organic Compounds in Some Workplace.
Hyo Min LEE ; Myung Soo KIM ; Shin Ai CHOI ; Eun Kyung YOO ; Jong Sei PARK
Korean Journal of Preventive Medicine 1997;30(3):530-539
This study was conducted to assess the health risk on the volatile organic compounds such as toluene, xylene, and styrene in painting workplace. It was monitored through personal air sampling during working time in selected 5 workplaces and analysed using gas chromatography. For the settlement of exposure situation, there were regarded working conditions such as working hours, yearly working days, and working years. Also, Monte-Carlo simulation was used for the induction of hazard index using toxicity value from IRIS(Integrated risk information system) database. The results of risk assessment were summarized as follows : 1. The air concentration of toluene was 7.096+/-15.6 ppm, 2.586+/-4.2 ppm for xylene, 1.914+/-5.3 ppm for styrene in blast painting workplaces. The level of toluene was different significantly compared with the level of xylene and styrene. 2. Computated chronic daily intake value of 95th percentile on toluene, xylene and styrene treated by Monte-Carlo simulation were 9.616, 3.567, 2.782 mg/kg/day, respectively. 3. Computated hazard index value of 75th percentile on toluene, xylene and styrene treated by Monte-Carlo simulation were 3.5, 1.0 and 1.6, respectively. Adverse health effects on the toluene, xylene and styrene would be expected by working exposure in blast painting workplace since the hazard indices of three compounds were exceeded 1 in the surroundings of percenitile 75 through having the low emerged frequency
Chromatography, Gas
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Humans
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Paint
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Paintings
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Risk Assessment*
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Styrene
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Toluene
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Volatile Organic Compounds*
;
Xylenes
8.Study of the removal difference in indoor particulate matter and volatile organic compounds through the application of plants.
Seung Han HONG ; Jiyeon HONG ; Jihyeon YU ; Youngwook LIM
Environmental Health and Toxicology 2017;32(1):e2017006-
This study was conducted to evaluate the ability of plants to purify indoor air by observing the effective reduction rate among pollutant types of particulate matter (PM) and volatile organic compounds (VOCs). PM and four types of VOCs were measured in a new building that is less than three years old and under three different conditions: before applying the plant, after applying the plant, and a room without a plant. The removal rate of each pollutant type due to the plant was also compared and analyzed. In the case of indoor PM, the removal effect was negligible because of outdoor influence. However, 9% of benzene, 75% of ethylbenzene, 72% of xylene, 75% of styrene, 50% of formaldehyde, 36% of acetaldehyde, 35% of acrolein with acetone, and 85% of toluene were reduced. The purification of indoor air by natural ventilation is meaningless because the ambient PM concentration has recently been high. However, contamination by gaseous materials such as VOCs can effectively be removed through the application of plants.
Acetaldehyde
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Acetone
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Acrolein
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Benzene
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Formaldehyde
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Particulate Matter*
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Plants
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Styrene
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Toluene
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Ventilation
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Volatile Organic Compounds*
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Xylenes
9.The Effects of Indoor Air Quality on the Neurobehavioral Performance of Elementary School Children.
Dae Seop KIM ; Sun Ju KIM ; Si Young PARK ; Man Joong JEON ; Gyu Tae KIM ; Chang Yoon KIM ; Jong Hak CHUNG ; Sung Ok BAEK ; Joon SAKONG
Korean Journal of Occupational and Environmental Medicine 2007;19(1):65-72
OBJECTIVES: Most studies on the indoor air quality of newly built schools have focused only on the number of schools exceeding a standard or on subjective symptoms, such as sneezing, irritated eyes and an irritated nose. However, there has been no report on how poor indoor air quality affects children's academic performance. This study evaluated the effects of indoor air quality on the neurobehavioral performance of elementary school children. METHODS: This study measured the indoor air pollutants and compared children's performance, using a computerized neurobehavioral test, between a newly built and a 12-year-old school. In addition, a questionnaire was administered regarding the indoor air quality related symptoms of children in a newly built and a 12-year-old school. RESULTS: In the newly built school, the formaldehyde levels in the 1st and 4th classes with an open window were 34.6 and 27.3 microgram/m3, respectively. The levels in the 1st and 4th classes with the window closed were 80.2 and 127.1 microgram/m3, respectively. In the 12-year-old school, the formaldehyde levels in 1st and 4th class with open and closed window were 12.6 and 7.5 microgram/m3, and 19.8 and 25.2 microgram/m3, respectively. With respect to total volatile organic compounds, the levels in the 1st and 4th classes with the window open in the newly built school were 87.2 and 428.2 microgram/m3, respectively. In the 1st and 4th classes with the window closed, the total volatile organic compounds were 1,283.5 and 1,715.4 microgram/m3, respectively. In the 12-year-old school, the total volatile organic compounds were 240.9 and 150.8 microgram/m3, and 371.9 and 448.0 microgram/m3 in the 1st and 4th classes, respectively. In the case of a newly built school, the performance of the students in the neurobehavioral test in the 4th class with the window closed was 8.3% lower than for those in the 1st class with the window closed, but was only 5.9% lower when the windows were open. There was a statistical significant difference in the total numbers of symptoms between the two schools. CONCLUSIONS: These results suggest a proper evaluation of the indoor air quality within schools is required into both the level of contamination and the health effects of these contaminants toward children.
Air Pollutants
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Air Pollution, Indoor*
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Child*
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Formaldehyde
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Humans
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Nose
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Questionnaires
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Sneezing
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Volatile Organic Compounds
10.Human Health Risk Assessment of Trichloroethylene from Industrial Complex A.
Toxicological Research 2012;28(3):173-178
This study investigated the human health risks of trichloroethylene from Industrial Complex A. The excessive carcinogenic risks for central tendency exposure were 1.40 x 10(-5) for male and female residents in the vicinity of Industrial Complex A. The excessive cancers risk for reasonable maximum exposure were 2.88 x 10(-5) and 1.97 x 10(-5) for males and females, respectively. These values indicate that there are potential cancer risks for exposure to these concentrations. The hazard index for central tendency exposure to trichloroethylene was 1.71 for male and female residents. The hazard indexes for reasonable maximum exposure were 3.27 and 2.41 for males and females, respectively. These values were over one, which is equivalent to the threshold value. This result showed that adverse cancer and non-cancer health effects may occur and that some risk management of trichloroethylene from Industrial Complex A was needed.
Female
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Humans
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Male
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Risk Assessment
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Risk Management
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Trichloroethylene
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Volatile Organic Compounds