• 한국산업보건학회지
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• 제7권2호
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• pp.161-170
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• 1997

본 연구는 사업장 근로자의 스타이렌 폭로수준과 이에 따른 biological monitoring 농도의 변화를 알기 위하여 시도되었다. 조사대상자는 FRP공장, 함침작업공장, 피막도포작업공장에 종사하는 남자근로자 64명과 여자근로자 44명이며 포집 및 분석기간은 1995년 6월 15일부터 9월 30일까지 였다. 일반적 특성중 연령, 성별, 근무경력, 음주량, 흡연량은 설문지를 이용하였고 신장과 체중은 개인건강기록표를, 스타이렌 환경폭로농도를 알기 위하여는 확산형 포집기를 사용하였으며, 생물학적 감시물질의 폭로수준을 알기 위하여 혈액과 소변을 채취하여 혈중 스타이렌, 요중 mandelic acid(MA)와 phenylglyoxylic acid(PGA)을 분석하였다. 평균폭로농도는 21.0ppm으로 저농도였으며 사업장별로는 선박관련업체가, 작업방법으로는 적층작업이, 작업형태는 주작업에서 가장 높은 폭로를 보였으며 대상자 중 11%가 허용기준 이상으로 폭로되었다. 환경폭로수준과 혈중 스타이렌의 상관성은 0.620이었고 creatinine으로 보정한 phenylglyoxylic acid와는 0.702로 가장 높은 상관성을 보였다. 혈중 스타이렌과 요중 대사산물의 상관관계는 MA+PGA에서 가장 높은 상관성을 보였다. 생물학적 대사산물의 변화를 설명하는 독립변수들 중 환경폭로농도가 가장 중요하였으며 특히 MA와 MA+PGA에서는 성별 역시 중요한 변수였다. 생물학적 대사산물에 대한 독립변수의 설명력은 모두 31% 이상이었으며 그중 혈중 스타이렌은 49.1%로 가장 높았다. 요중 대사산물을 보정여부에 따른 상관성을 본 결과 모두 0.95이상을 보였다. 이상을 종합한 바 스타이렌 취급작업장의 공기중 농도를 측정할 때 확산포집기로도 사용할 수 있으며, 요의 생물학적 지표에서는 비중으로 보정한 경우가 creatinine으로 보정한 것의 대안으로 사용할 수 있고 또한 요중 MA 및 PGA를 이용하여 폭로 근로자의 폭로농도를 예측할 수 있으므로 이를 스타이렌 취급근로자에 적극적인 활용이 필요한 것으로 제시할 수 있다.

• Environmental Analysis Health and Toxicology
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• 제17권3호
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• pp.197-205
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• 2002

Volatile organic compounds (VOCs) are an important public health problem throughout the world. Many important questions remain to be addressed in assessing exposure to these compounds. Because they are ubiquitous and highly volatile, special techniques must be applied in the analytical determination of VOCs. Personal exposure measurements are needed to evaluate the relationship between microenvironmental concentrations and actual exposures. It is also important to investigate exposure frequency, duration, and intensity, as well as personal exposure characteristics. In addition to air monitoring, biological monitoring may contribute significantly to risk assessment by allowing estimation of absorbed doses, rather than just the external exposure concentrations, which are evaluated by environmental and personal monitoring. This study was conducted to establish the analytic procedure of VOCs in air, blood, urine and exhaled breath and to evaluate the relationships among these environmental media. The subjects of this study were selected because they are occupationally exposed to high levels of VOCs. Environmental, personal, blood, urine and exhalation samples were collected. Purge ＆ trap, thermal desorber, gas chromatography and mass selective detector were used to analyze the collected samples. Analytical procedures were validated with the“break through test”, 'quot;recovery test for storage and transportation”,“method detection limit test”and“inter-laboratory QA/QC study”. Assessment of halogenated compounds indicted that they were significantly correlated to each other (p value < 0.01). In a similar manner, aromatic compounds were also correlated, except in urine sample. Linear regression was used to evaluate the relationships between personal exposures and environmental concentrations. These relationships for aromatic and halogenated are as follows: Halogen $s_{personal}$ = 3.875+0.068Halogen $s_{environmet}$, ($R^2$= .930) Aromatic $s_{personal}$ = 34217.757-31.266Aromatic $s_{environmet}$, ($R^2$= .821) Multiple regression was used to evaluate the relationship between exposures and various exposure deter-minants including, gender, duration of employment, and smoking history. The results of the regression model-ins for halogens in blood and aromatics in urine are as follows: Halogen $s_{blood}$ = 8.181+0.246Halogen $s_{personal}$+3.975Gender ($R^2$= .925), Aromatic $s_{urine}$ = 249.565+0.135Aromatic $s_{personal}$ -5.651 D.S ($R^2$ = .735), In conclusion, we have established analytic procedures for VOC measurement in biological and environmental samples and have presented data demonstrating relationships between VOCs levels in biological media and environmental samples. Abbreviation GC/MS, Gas Chromatography/Mass Spectrometer; VOCs, Volatile Organic Compounds; OVM, Organic Vapor Monitor; TO, Toxic Organicsapor Monitor; TO, Toxic Organics.

• 한국산업보건학회지
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• 제11권1호
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• pp.34-41
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• 2001

Passive samplers have been used for personal, indoor, and outdoor air monitoring of VOCs at ppb concentrations in community and office environments. The path length of modified passive sampler was shortened, so it was intended to increase an uptake rate. The performance of the modified 3M 3500 organic vapor monitor(OVM) as a tool for assessing exposures to toxic air pollutants in nonoccupational community environments was evaluated using combined controlled test atmospheres of six selected target volatile organic compounds(VOCs): benzene, methyl tert-butyl ether(MTBE), chloroform, 1,4-dichlorobenzene, tetrachloroethylene, and toluene. The experiments were conducted by exposing the dosimeters to concentrations of $50{\sim}100{\mu}g/m^3$ on six face velocity(0.00, 0.02, 0.06, 0.12, 0.20, 0.30 m/sec) for 24 hours. If the uptake rate was increased, that means that we could use the passive sampler more effectively. The uptake rates were increased linearly according to reduce the path length. Although the diffusion path length was shortened, the change of uptake rate was within ${\pm}25%$ of theoretical value, indicating that the modified passive sampler(TM) can be effectively used over the range of concentrations and environmental conditions tested with a 24-h sampling period if the face velocities were over 0.12 m/s for 6 components of VOCs. But when the face velocities were less than 0.12 m/s, uptake rates were reduced more than expected values. So, the passive sampler with the shortened path length should be used at indoor or outdoor environment where the face velocity should be over about 0.10 m/s. If the path length was shortened more, the uptake rate was more effected by starvation.