공단지역 일부 주민들의 주택유형 및 실내/외에 따른 VOCs(Benzene, Toluene, Xylene) 농도 및 상관성에 관한 연구
DC Field | Value | Language |
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dc.contributor.author | 이치원 | - |
dc.contributor.author | 전혜리 | - |
dc.contributor.author | 홍은주 | - |
dc.contributor.author | 유승도 | - |
dc.contributor.author | 김대선 | - |
dc.contributor.author | 손부순 | - |
dc.date.accessioned | 2021-08-12T07:27:37Z | - |
dc.date.available | 2021-08-12T07:27:37Z | - |
dc.date.issued | 2010 | - |
dc.identifier.issn | 1738-4087 | - |
dc.identifier.issn | 2233-8616 | - |
dc.identifier.uri | https://scholarworks.bwise.kr/sch/handle/2021.sw.sch/18255 | - |
dc.description.abstract | The objectives of this study were to understand the characteristics of residents in industrial areas and factors affecting exposure to the Volatile Organic Compounds(VOCs : Benzene, Toluene, Xylene) as well as to assess exposure levels according to house-type, and whether residents were indoors or outdoors. This research was designed to assess the differences in exposure levels to indoor, outdoor and personal VOCs in a case group and a control group across all areas,as well as in each different area, from May to October 2007, in. 110 residents of the G, Y and H industrial areas of the Jun-nam province. The geometric mea-levels of airborne benzene for the case group 1.31part per billion(ppb) indoor,1.29 ppb outdoor, and 1.32 ppb for personal exposure were significantly higher than for the control group 0.99, 0.87 and 0.57 ppb, respectively. The geometric mean level for toluene personal exposure across the G, Y and H areas was 5.70 ppb for the case group and 6.31 ppb for the control group. While the outdoor level was 4.27 ppb for the case group and 5.06 ppb for the control group, The indoor level for the case group was 4.78 ppb, similar to that of the control group 4.69 ppb. The geometric mean levels for airborne xylene across the G, Y and H areas were 0.16 ppb(outdoor),0.12 ppb(personal exposure) and 0.10 ppb(indoor) for the case group, and for the control group were 0.17(personal exposure) and 0.09 ppb(indoor and outdoor). The indoor/outdoor(I/O) ratio for case group is 1.19, while that of the control group is 1.15, indicating that the indoor level was higher than the outdoor level. The interrelationship differences among the three different types of levels in the air in the G, Y and H areas are statistically significant, except for the difference between the indoor and outdoor figures for xylene. In terms of the different types of houses and energy type uesd, the geometric mean level for airborne benzene, toluene and xylene for houses were 1.61, 5.39 and 0.12 ppb,respectively. while the figures for flats were 0.67, 3.32 and 0.05 ppb, respectively. Outdoors, the levels of benzene and toluene in flats were 0.71 and 2.62 ppb, respectively. and 1.58 and 5.35 ppb in houses. For personal exposure, the house levels of benzene, toluene and xylene were all higher than for flats. Houses using oil for heating have significantly higher levels than flats, which use gas for heating. | - |
dc.format.extent | 9 | - |
dc.language | 한국어 | - |
dc.language.iso | KOR | - |
dc.publisher | 한국환경보건학회 | - |
dc.title | 공단지역 일부 주민들의 주택유형 및 실내/외에 따른 VOCs(Benzene, Toluene, Xylene) 농도 및 상관성에 관한 연구 | - |
dc.title.alternative | A Study on the Correlation and Concentration in Volatile Organic Compounds(Benzene, Toluene, Xylene) Levels According to the Indoor/Outdoor and the Type of Residents' House in Industrial Area | - |
dc.type | Article | - |
dc.publisher.location | 대한민국 | - |
dc.identifier.bibliographicCitation | 한국환경보건학회지, v.36, no.5, pp 351 - 359 | - |
dc.citation.title | 한국환경보건학회지 | - |
dc.citation.volume | 36 | - |
dc.citation.number | 5 | - |
dc.citation.startPage | 351 | - |
dc.citation.endPage | 359 | - |
dc.identifier.kciid | ART001492093 | - |
dc.description.isOpenAccess | N | - |
dc.description.journalRegisteredClass | kci | - |
dc.subject.keywordAuthor | VOCs | - |
dc.subject.keywordAuthor | personal exposure | - |
dc.subject.keywordAuthor | control | - |
dc.subject.keywordAuthor | case | - |
dc.subject.keywordAuthor | geometric mean | - |
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