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Abstract 10
1. 서론 12
1.1. 연구배경 및 목적 12
1.2. 이론적 고찰 15
1.2.1. Polychlorinated dibenzo-para-dioxins and polychlorinated dibenzofurans(PCDD/DFs) 15
1.2.2. Dioxin like Polychlorinated biphenyls(DL-PCBs) 20
1.2.3. Polycyclic aromatic hydrocarbons(PAHs) 23
1.3. CMB 모델 27
1.3.1. CMB 모델의 개요 27
1.3.2. CMB 모델의 국내·외 연구사례 31
2. 실험방법 33
2.1. 시료 채취 및 전처리 방법 33
2.1.1. 대기시료 33
2.1.2. PAHs 발생원 시료 40
2.2. 분석조건 및 방법 42
2.2.1. PCDD/DFs 42
2.2.2. DL-PCBs 45
2.2.3. PAHs 46
3. 결과 및 고찰 48
3.1. 산업단지별 다이옥신류 프로파일 특성 48
3.2. 산업단지별 PAHs 농도수준 및 프로파일 특성 56
3.3. PAHs 발생원 정의 및 기여도 평가 64
3.3.1. PAHs의 주요 발생원 분류 및 배출특성 66
3.3.2. PCA를 통한 PAHs 발생원 정의 83
3.3.3. 특성분석의 발생원 정의 85
3.3.4. CMB모델을 이용한 발생원 기여도 할당 91
4. 요약 및 향후 연구방안 97
참고문헌 101
감사의 글 116
Fig. 1. Molecular structures of toxic 2,3,7,8-substituted PCDD/DFs. 19
Fig. 2. Molecular structures and numbering systems of PCBs. 21
Fig. 3. Sampling location of this study. 34
Fig. 4. Multi-layer silica gel column chromatography(upper) and activated alumina column chromatography(lower) for PCDD/DFs analysis. 38
Fig. 5. Experimental procedures for the determination of PAHs. 39
Fig. 6. Profile pattern of total of 2,3,7,8 substituted PCDD/DFs in Ambient air of Industrial complex.[원문불량] 50
Fig. 7. Profile pattern of total of PCDD/DFs homologue in Ambient air of industrial complex. 51
Fig. 8. Homologue profile pattern of PCDD/DFs in each seasons. 53
Fig. 9. Profile of DL-PCBs. 55
Fig. 10. Profile of PAHs 59
Fig. 11. Contribution rate of Carc.PAHs(upper) and benzene ring PAHs(lower). 61
Fig. 12. Principal component analysis about PCDD/DFs, DL-PCBS, PAHs from Ambient air of industrial area. 63
Fig. 13. Concentration of ΣPAHs(upper) and Profile pattern(lower) in each waste incinerator. 68
Fig. 14. Contribution rate of each ring number 16 PAHs(upper) and PAHcarc(lower) in waste incinerators. 69
Fig. 15. Concentration of ΣPAHs(upper) and Profile pattern(lower) in each iron/steel and nonferrous industry. 71
Fig. 16. Contribution rate of each ring number 16 PAHs(upper) and PAHcarc(lower) in Iron/steel and nonferrous industry. 72
Fig. 17. Concentration of ΣPAHs(upper) and Profile pattern(lower) in each iron/steel and nonferrous industry. 74
Fig. 18. Contribution of each ring number 16 PAHs(upper) and PAHcarc(lower) in Chemical industry. 75
Fig. 19. Profiles of PAHs compounds in each sources. 79
Fig. 20. Principal component analysis about PAHs sources. 82
Fig. 21. Principal component analysis about PAHs sources and Industrial complex ambient air. 84
Fig. 22. “Diagnostic ratios" for a variety of source categories for 6 indicators. 88
Fig. 23. Correlation between calculated and observed concentration of PAHs in ambient air of the Industrial complex. 94
Fig. 24. Source contributions(%) for PAHs in ambient air of industrial area, Korea. 96
PCDD/DFs released to the atmosphere are mainly emitted from anthropogenic activities, including waste incineration, power/energy generation, other high-temperature sources and chemical-industrial sources. Furthermore, polycyclic aromatic hydrocarbons (PAHs) are emitted to the atmosphere from variety sources. Therefore, it is important to evaluate quantitatively the relationship between receptor and sources for effective control about pollutants.
In this study, ambient air samples are collected from 7 highly industrialized area(A∼G) in Korea. Major PAHs sources such as waste incinerator, iron/steel and nonferrous industry, chemical industry were examined and the reference data from other sources such as open burning, crematory, road dust, vehicle exhaust, boiler and briquette was quoted from previous study in Korea.
The first purpose of this study is to evaluate the characteristic of PCDD/DFs, DL-PCBs and PAHs on ambient air of industrial area.
Second purpose is to examine the characteristic of PAHs profile pattern on PAHs sources. PAHs sources were identified with PCA and diagnostic ratio analysis about the ambient air in industrial area and PAHs air emission sources.
Finally, A chemical mass balance model, CMB8.2 was used to apportion the major sources of PAHs detected in ambient air of industrial area. The coefficient of determination R², χ² and percent mass were average 0.99, 1.42 and 83.25%, respectively. Therefore these results of CMB model were confirmed statistically valuable. Modeling results verified that chemical industry and iron/steel and nonferrous industry are major sources of PAHs in this study.
keywords : PCDD/DFs , PAHs, Industrial area, Source identification, PCA, CMB model*표시는 필수 입력사항입니다.
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