PUKYONG

환경 중 잔류성유기오염물질의 분포 특성 및 오염원 추정

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Alternative Title
Distribution characteristics and source estimation of persistent organic pollutants(POPs) in environment
Abstract
This study was performed to investigate the persistent status of POPs in Korea using environment medias such as air, soil, water and the surface sediment. Also the study identified the source and fugacity of POPs using congener analyses of PCDD/Fs and OCPs, principal component analysis(PCA) and Cluster analysis(CA). The obtained results are summarized as follow;
As a comprehensive monitoring survey on POPs in korea, 111 ambient air samples taken from 37 locations during four different seasons were studied. PCDD/Fs concentrations ranged from 0.067 to 12.41 pg/Sm3, and WHO-TEQ values ranged from 0.003 to 0.285 pg/Sm3WHO-TEQ. In all samples, the dominant congeners were OCDD, 1,2,3,4,6,7,8-HpCDF, 1,2,3,4,6,7,8-HpCDD, OCDF and 2,3,4,7,8-PeCDF, and the congener profiles did not display any seasonal trend. According to Principal component analyses, dioxin emissions in ambient air assumed to be originated from flue gas, vehicle and sinter plants.
The concentrations of OCPs exhibited the highest in summer due to volatilization of OCPs to the ambient air from other environment media, such as soil. However, there was no concentration variation related to temperature in Chlordane. For each chlordane compound, the concentration of trans-Chlordane was 1.586 times higher than that of cis-Chlordane. According to the results, it is possible to assume that Chlordanes found in Korean ambient air are not residue of early usage, but from recent usage in remote areas.
For DDTs, the concentration ratio of p,p’-DDT and the degrading metabolite p,p’-DDE were determined to discover the source of DDTs. The average ratio of p,p’-DDT/p,p’-DDE was relatively low (about0.341) which means there is no significant input of fresh DDT, and that the degrading of residues are processing.
POPs were analyzed in soils collected from 57 sites. The concentrations of PCDD/Fs ranged from 0.06 to 10.43 pg WHO-TEQ /g d.w (mean value, 1.35 pg WHO-TEQ /g), and the concentrations of DL-PCBs ranged from ND to 3.50 pg WHO-TEQ /g d.w (mean value, 0.97 pg WHO-TEQ/ g). The TEQ concentrations were as follow: industrial area > rural area > suburban area > urban area. In terms of congener distribution, OCDD was predominant congener with the various fraction (from 27 to 84%). The ratio of PCDF to PCDD ranged from 0.06 to 1.25.
POPs were analyzed in surface sediments and river water collected from each 30 and 36 sites, respectively. The concentrations of PCDD/Fs ranged from 0,001 to 3.828 pg WHO-TEQ/g (mean value, 0.860 pg WHO-TEQ/g) in surface sediment. In river water, the concentrations of PCDD/F ranged from 0,002 to 0.966 pg WHO-TEQ/L (mean value, 0.095 pg WHO-TEQ/L).
Backward trajectories was conducted to show the pathways of air particles using HYSPLIT4 (Hybrid Single Particle Lagrangian Integrated Trajectory, Version 4) model with FNL meteorological data.
In this study, the movement pathways of local or regional pollutants were estimated at 50m AGL within the surface layer. 72 hours backward trajectories were computed each hour, from noon to noon, starting at 50m AGL.
This study was completed in order to investigate the equilibrium of PCDD/Fs in air and soil, and to know whether soil is a secondary source of PCDD/Fs pollution in air. The relationship between molecular weight, vapor pressure(PL) and octanol-air partition coefficient (Kow) to the PCDD/Fs concentration of air(Cair) and soil(Csoil) were unclear. The slope of the regression line between soil-air partition coefficient (Ksa) and scavenging coefficient (Csoil/Cair) ranged from 0.202 to 2.1462, and the PCDD/Fs concentration between air and soil did not reached to the equilibrium state. The soil/air fugacity quotients (fsoil/fair) of low chlorinated compounds (2,3,7,8-TCDD, 2,3,7,8,-TCDF, 1,2,3,7,8-PeCDF and 2,3,4,7,8-PeCDF), were less than 1, while fsoil/fair of high chlorinated compounds were (1,2,3,7,8,9-HxCDD, 1,2,3,4,6,7,8-HpCDD and OCDD, OCDF) were greater than 1. Such result is highly effected by the deposition of PCDD/Fs from air to soil.

Key words: PCDD/Fs, DL-PCBs, OCPs, PCA, Fugacity
Author(s)
정봉길
Issued Date
2011
Awarded Date
2011. 2
Type
Dissertation
Publisher
부경대학교
URI
https://repository.pknu.ac.kr:8443/handle/2021.oak/9909
http://pknu.dcollection.net/jsp/common/DcLoOrgPer.jsp?sItemId=000001964172
Alternative Author(s)
Bong-Gil Jung
Department
대학원 지구환경공학학ㆍ연협동과정
Advisor
옥곤
Table Of Contents
제1장 서 론 5
1.1. 연구배경 및 목적 5
1.2. 연구범위 및 구성 9
제2장 문헌 조사 12
2.1. POPs의 개요 12
2.1.1. 다이옥신류의 물리․화학적 특성 12
2.1.2. 유기염소계농약류(OCPs)의 물리․화학적 특성 20
2.2. 환경 중 POPs의 거동 31
2.2.1. 대기 중 POPs의 거동 31
2.2.2. 토양 중 POPs의 거동 38
2.2.3. 수계 중 POPs의 거동 41
2.2.4. 물리․화학적 Parameter 41
제3장 시료채취 및 분석방법 47
3.1. 시료 채취지점의 선정 47
3.1.1. 대기 시료 채취지점 47
3.1.2. 토양 시료 채취지점 51
3.1.3. 수질 및 퇴적물 시료 채취지점 55
3.2. 시료 채취방법 59
3.2.1. 대기시료 채취 59
3.2.2. 수질시료 채취 60
3.2.3. 토양 및 퇴적물시료 채취 60
3.2.4. 토양 시료의 환경 특성 인자 분석 63
3.3. 분석방법 65
3.3.1. 다이옥신 및 퓨란류, DL-PCBs 분석방법 65
3.3.2. 유기염소계 농약류 분석방법 70
3.3.3. 기기분석 76
3.3.4. 정도관리 81
3.3.5. 물질별 분석방법 검출한계 93
3.4. 오염현상 해석을 위한 통계적 평가기법 97
3.4.1. 주성분 분석 98
3.4.2. 군집분석(Cluster Analysis) 102
제4장 환경매체 중 POPs의 농도수준 및 특성 104
4.1. 대기 중 POPs 104
4.1.1. 대기 중 다이옥신류의 농도수준 및 특성 104
4.1.2. 대기 중 유기염소계농약류의 농도수준 및 특성 117
4.1.3. 대기 중 POPs의 기상인자의 영향 145
4.1.4. 궤적분석에 의한 공기의 기원 148
4.2. 토양 중 POPs 156
4.2.1. 토양 중 다이옥신류의 농도수준 및 특성 156
4.2.2. 토양 중 유기염소계농약류의 농도수준 및 특성 166
4.3. 수계 중 POPs 169
4.3.1. 수계 중 다이옥신류의 농도수준 및 특성 169
4.3.2. 수계 중 유기염소계농약류의 농도수준 및 특성 177
제5장 POPs의 오염원 해석 178
5.1. 이성질체 유형 비교에 의한 영향 분석 178
5.2. 통계적 처리기법에 의한 영향 분석 183
5.2.1. 대기 183
5.2.2. 토양 186
5.2.3. 퇴적물 191
제6장 매체간 이동 194
6.1. 대기에서의 다이옥신류 침적량 추정 194
6.2. 대기-토양 중 fugacity 198
제7장 결론 및 제안 204
7.1. 결 론 204
7.2. 향후 연구를 위한 제안 209
Degree
Doctor
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