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      일반대기 중 극미세입자와 중금속 농도에 관한 연구 = A Study on the Size of Ultrafine Particles and Heavy Metal Concentrations in the Atmosphere

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      https://www.riss.kr/link?id=A103755070

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      다국어 초록 (Multilingual Abstract)

      This study evaluated the distribution of the concentrations of nano-particles and heavy metals (08-Pb, Cr, Zn, As, Fe, 09-Pb, Cr, Zn, Cu, Ni, Mn) in Seoul, Chungnam A and Gwangyang from August to December, in 2008 5 times each in the Seoul area, 5 tim...

      This study evaluated the distribution of the concentrations of nano-particles and heavy metals (08-Pb, Cr, Zn, As, Fe, 09-Pb, Cr, Zn, Cu, Ni, Mn) in Seoul, Chungnam A and Gwangyang from August to December, in 2008 5 times each in the Seoul area, 5 times in and Chungnam A area and from August to November, in 2009 14 times in the Chungnam A area, 8 times in the Gwangyang area. The examined results showed high concentration level from $PM_1$ through $PM_{0.1}$ in all three areas. These results were obtained the concentration of particles by diameter and statistically significant in Stage5 (1.0-0.56 ${\mu}m$) from the result of conducting Kruskal-Wallis H test (p < 0.05). In the case of the heavy metal concentration included in 0.10-0.056 ${\mu}m$, 0.056 ${\mu}m$, the lead concentration of Chungnam Asan area was 6.49 ng/$m^3$ and 9.93 ng/$m^3$, which was higher than 3.05 ng/$m^3$ and 4.22 ng/$m^3$ of Seoul, respectively. The concentration of iron in Seoul was 9.28 ng/$m^3$ and 13.24 ng/$m^3$, that appeared higher than 2.38 ng/$m^3$ and 3.23 ng/$m^3$ of Chungnam A area, respectively. The concentration level was similar to other metals except lead and iron in Chungnam A area and Seoul. From the concentration of heavy metal included in 0.10-0.056 ${\mu}m$, 0.056 ${\mu}m$, the lead concentration of Chungnam A area was 0.31 ng/$m^3$ and 0.12 ng/$m^3$ while Gwangyang was 0.28 ng/$m^3$, 0.06 ng/$m^3$. Thus Chungnam A area showed higher lead concentration than Gwangyang. The manganese concentration of Chungnam A area was 0.12 ng/$m^3$ and 0.03 ng/$m^3$ while Gwangyang was 0.21 ng/$m^3$ and 0.08 ng/$m^3$. Therefore, the concentration of Gwangyang appeared higher than that of Chunnam A area. These two metals showed statistically significant in 0.056 ${\mu}m$ (p < 0.05, p < 0.01). Among the concentration of heavy metal in all regions, the result demonstrated that the order of higher concentration is arsenic > iron > zinc > chrome > lead > nickel > copper > manganese.

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      참고문헌 (Reference)

      1 강공언, "황사 에피소드 발생시 대기먼지의 농도 특성과 인체 영향" 한국환경보건학회 35 (35): 21-35, 2009

      2 백성옥, "포항지역 대기 중 초미세먼지(PM2.5)의 오염특성평가" 대한환경공학회 30 (30): 302-313, 2008

      3 Park, K. H, "Studies on sizeresolvedhygroscopic properties of fine aerosol particlesin the atlanta ambient atmosphere"

      4 Allen, A. G, "Size distributions of tracemetals in atmospheric aerosols in the United Kingdom" 35 : 4581-4591, 2001

      5 Cheng, Y, "Seasonal and diurnal variations of PM1.0, PM2.5 andPM10 in the roadside environment of Hong Kong" 4 (4): 312-315, 2006

      6 Muller, J, "Respiratory toxicity of multi-wallcarbon nanotubes" 207 : 221-231, 2005

      7 Thomas, K, "Research strategies forsafety evaluation of nanomaterials, Part I: Evaluatingthe human health implications of exposure to nanoscalematerials" 87 (87): 316-321, 2005

      8 Donaldson,K, "Potential mechanismsof adverse pulmonary and cardiovasculareffects of particulate air pollution (PM10)" 203 : 411-415, 2001

      9 Yoon, C. S, "Potential health risks and issues ofnanoparticles" Biochemistry and Molecular BiologyNews 8-21, 2007

      10 Kim, K. H, "PM2.5, PM10, TSP, based on observationsover time of dust particles during the study onthe characteristics of the distribution: of the four stationsaround Seoul, a 2001 case study on the durationof the spring dust" 18 (18): 419-426, 2002

      1 강공언, "황사 에피소드 발생시 대기먼지의 농도 특성과 인체 영향" 한국환경보건학회 35 (35): 21-35, 2009

      2 백성옥, "포항지역 대기 중 초미세먼지(PM2.5)의 오염특성평가" 대한환경공학회 30 (30): 302-313, 2008

      3 Park, K. H, "Studies on sizeresolvedhygroscopic properties of fine aerosol particlesin the atlanta ambient atmosphere"

      4 Allen, A. G, "Size distributions of tracemetals in atmospheric aerosols in the United Kingdom" 35 : 4581-4591, 2001

      5 Cheng, Y, "Seasonal and diurnal variations of PM1.0, PM2.5 andPM10 in the roadside environment of Hong Kong" 4 (4): 312-315, 2006

      6 Muller, J, "Respiratory toxicity of multi-wallcarbon nanotubes" 207 : 221-231, 2005

      7 Thomas, K, "Research strategies forsafety evaluation of nanomaterials, Part I: Evaluatingthe human health implications of exposure to nanoscalematerials" 87 (87): 316-321, 2005

      8 Donaldson,K, "Potential mechanismsof adverse pulmonary and cardiovasculareffects of particulate air pollution (PM10)" 203 : 411-415, 2001

      9 Yoon, C. S, "Potential health risks and issues ofnanoparticles" Biochemistry and Molecular BiologyNews 8-21, 2007

      10 Kim, K. H, "PM2.5, PM10, TSP, based on observationsover time of dust particles during the study onthe characteristics of the distribution: of the four stationsaround Seoul, a 2001 case study on the durationof the spring dust" 18 (18): 419-426, 2002

      11 Cabada, J. C, "Mass size distributions and size resolved chemicalcomposition of fine particulate matter at the Pittsburghsupersite" 38 : 3127-3141, 2004

      12 Lee, M. Y, "Development of molecular level biomarkersagainst the risk assessment of heavy metals inthe air-borne nanoparticles through metalloproteomictechnology"

      13 Montaya, L, "Continuous measurementsof ambient particle deposition in human subjects" 38 : 980-990, 2004

      14 Fang, G. C, "Concentrationsof nano and related ambient air pollutants at atraffic sampling site" 21 : 259-271, 2005

      15 Lee, H. B, "Characteristics of atmospheric aerosols inChungnam, Korea"

      16 Gong, M. H, "Asan and Seoul in some areas fineparticles (PM2.5) concentration and composition ofmetals"

      17 Kim, K. H, "Air Pollution Test Methods for EnvironmentalAnalysis" Donghwa Technology 313-364, 2000

      18 Choi, D. M, "A source identification and characteristicsby the airborne heavy metals of cement factoryoutskirts area inhabitants"

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      학술지 이력

      학술지 이력
      연월일 이력구분 이력상세 등재구분
      2022 평가예정 계속평가 신청대상 (등재유지)
      2017-01-01 평가 우수등재학술지 선정 (계속평가)
      2013-01-01 평가 등재 1차 FAIL (등재유지) KCI등재
      2010-01-01 평가 등재학술지 유지 (등재유지) KCI등재
      2008-02-15 학술지명변경 외국어명 : Korean Journal of Environmental Health -> JOURNAL OF ENVIRONMENTAL HEALTH SCIENCES KCI등재
      2008-01-01 평가 등재학술지 유지 (등재유지) KCI등재
      2006-01-01 평가 등재학술지 유지 (등재유지) KCI등재
      2005-09-13 학술지등록 한글명 : 한국환경보건학회지
      외국어명 : Korean Journal Of Environmental Health
      KCI등재
      2005-06-02 학술지등록 한글명 : 한국환경보건학회지
      외국어명 : Korean Journal of Environmental Health
      KCI등재
      2005-01-27 학회명변경 한글명 : 한국환경위생학회 -> 한국환경보건학회
      영문명 : Korean Society Of Environmental Health -> Korean Society of Environmental Health
      KCI등재
      2003-01-01 평가 등재학술지 선정 (등재후보2차) KCI등재
      2002-01-01 평가 등재후보 1차 PASS (등재후보1차) KCI등재후보
      1999-01-01 평가 등재후보학술지 선정 (신규평가) KCI등재후보
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      학술지 인용정보

      학술지 인용정보
      기준연도 WOS-KCI 통합IF(2년) KCIF(2년) KCIF(3년)
      2016 0.44 0.44 0.4
      KCIF(4년) KCIF(5년) 중심성지수(3년) 즉시성지수
      0.42 0.4 0.605 0.21
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