대학교 행정실 실내 외 공기 중 나노입자와 중금속 농도에 관한 연구
A Study on the Concentration of Nanoparticles and Heavy Metals in Indoor/Outdoor Air in a University Administrative Public Office
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초록
Objectives: The purpose of this study is to investigate the mass concentration of nanoparticles and understand the characteristics of elements of heavy metal concentrations within nanoparticles in the air using Micro-Orifice Uniform Deposit Impactor Model-110 (MOUDI-110), based on indoor and outdoor air. Methods: This Study sampled nanoparticles using MOUDI-110 indoors (office) and outdoors at S University in Asan, Korea in order to reveal the concentration of nanoparticles in the air. Sampling continued for nine months (10 times indoors and 14 times outdoors) from March to November 2010. Mass concentrations of nanoparticle and concentrations of heavy metals (Al, Mn, Zn, Ni, Cu, Cr, Pb) were analyzed. Results: Indoors, geometric mean concentration of nanoparticles ranged in size from 0.056 ㎛ to 0.10 ㎛ and those of 0.056 ㎛ or less recorded 0.929 ${\mu}g/m^3$ and 1.002 ${\mu}g/m^3$, respectively. On the other hand, the levels were lower outdoors with 0.819 ${\mu}g/m^3$ and 0.597 ${\mu}g/m^3$. Mann-Whitney U tests showed that the difference between the indoors and the outdoors was statistically meaningful in terms of particles of 0.056 ㎛ or less (p<0.05) in size. These results are possibly influenced by the use of printers and duplicators as the factor that increased the concentration of nanoparticles. In seasonal concentration distribution, the level was higher during the summer compared to in the autumn. Those of 0.056 ㎛ or less in size presented a statistically meaningful difference during the summer (p<0.05). These results may be influenced by photochemical event as the factor that makes the levels high. Regarding zinc, among the other heavy metals, the fine particles ranged in size from 0.056 ㎛ to 0.10 ㎛ and those of 0.056 ㎛ or less recorded 1.699 $ng/m^3$ and 1.189 $ng/m^3$ in the outdoors. In the indoors, the levels were lower, with 0.745 $ng/m^3$ and 0.617 $ng/m^3$. Cr and Ni at the size of 0.056 ㎛ or less, both of which have been known to pose severe health effects, recorded higher concentrations indoors with 0.736 $ng/m^3$ and 0.177 $ng/m^3$, compared to 0.444 $ng/m^3$ and 0.091 $ng/m^3$ outdoors. By season, Zn, Ni, Cu and Pb posted a high level of indoor concentration during the fall. As for Cr, the level of concentration indoors was higher than outdoors both during the summer and the autumn. Conclusion: This study indicates the result of an examination of nano-sized particles and heavy metal concentrations. It will provide useful data for the determination of basic nanoparticle standards in the future.
Abstract
Objectives: The purpose of this study is to investigate the mass concentration of nanoparticles and understand the characteristics of elements of heavy metal concentrations within nanoparticles in the air using Micro-Orifice Uniform Deposit Impactor Model-110 (MOUDI-110), based on indoor and outdoor air. Methods: This Study sampled nanoparticles using MOUDI-110 indoors (office) and outdoors at S University in Asan, Korea in order to reveal the concentration of nanoparticles in the air. Sampling continued for nine months (10 times indoors and 14 times outdoors) from March to November 2010. Mass concentrations of nanoparticle and concentrations of heavy metals (Al, Mn, Zn, Ni, Cu, Cr, Pb) were analyzed. Results: Indoors, geometric mean concentration of nanoparticles ranged in size from 0.056 ㎛ to 0.10 ㎛ and those of 0.056 ㎛ or less recorded 0.929 ${\mu}g/m^3$ and 1.002 ${\mu}g/m^3$, respectively. On the other hand, the levels were lower outdoors with 0.819 ${\mu}g/m^3$ and 0.597 ${\mu}g/m^3$. Mann-Whitney U tests showed that the difference between the indoors and the outdoors was statistically meaningful in terms of particles of 0.056 ㎛ or less (p<0.05) in size. These results are possibly influenced by the use of printers and duplicators as the factor that increased the concentration of nanoparticles. In seasonal concentration distribution, the level was higher during the summer compared to in the autumn. Those of 0.056 ㎛ or less in size presented a statistically meaningful difference during the summer (p<0.05). These results may be influenced by photochemical event as the factor that makes the levels high. Regarding zinc, among the other heavy metals, the fine particles ranged in size from 0.056 ㎛ to 0.10 ㎛ and those of 0.056 ㎛ or less recorded 1.699 $ng/m^3$ and 1.189 $ng/m^3$ in the outdoors. In the indoors, the levels were lower, with 0.745 $ng/m^3$ and 0.617 $ng/m^3$. Cr and Ni at the size of 0.056 ㎛ or less, both of which have been known to pose severe health effects, recorded higher concentrations indoors with 0.736 $ng/m^3$ and 0.177 $ng/m^3$, compared to 0.444 $ng/m^3$ and 0.091 $ng/m^3$ outdoors. By season, Zn, Ni, Cu and Pb posted a high level of indoor concentration during the fall. As for Cr, the level of concentration indoors was higher than outdoors both during the summer and the autumn. Conclusion: This study indicates the result of an examination of nano-sized particles and heavy metal concentrations. It will provide useful data for the determination of basic nanoparticle standards in the future.
참고문헌 (40)
- Hoddinott KB, "The use of environmental risk assessment methodologies for an indoor air quality investigation", Chemosphere, 41(1-2), pp.77~84 (2000)
- Statistics Korea, "Report on the time use survey", 1, pp.29~50 (2000)
- Sundell J., "On the history of indoor air quality and health", Indoor Air, 14(7), pp.51~58 (2004)
- Lee SD, "study on chemical composition of PM10 and PM2.5 in office buildings" (2006), Hanyang University
- Lee YM, "The distribution of fine particles in indoor", outdoor at elementary school in Incheon, 2008, 538~539
- Montoya L, "Continuous measurements of ambient particle deposition in human subjects", Aerosol Sci Technol, 38(10), pp.980~990 (2004)
- Park EJ., "Health risk assessment of fine particles and their hazardous chemicals" (2008), Dongduk Womens University
- U.S.EPA, "Air quality criteria for particulate matter" (2004), office of research and development
- Kulmala M, "Formation and growth rates of ultrafine atmospheric particles: a review of observations", J Aerosol Sci, 35(2), pp.143~176 (2004)
- "What is Nanotechnology?" (2004)[URL]
- U.S.EPA. Ministry of Environment., "Nanotechnology white paper" (2007)
- Morawska L, "Health impacts on ultrafine particles", Environment standards Branch, Department of the Environment and Heritage, ~ (2004)
- Elihn K, "Ultrafine particle characteristics in seven industrial plants", Ann Occup Hyg, 53(5), pp.475~484 (2009)
- Maynard AD, "Airborne nanostructured particles and occupational health", J Nanopart Res, 7(6), pp.587~614 (2005)
- Langer S, "Ultrafine particle produced by ozone", limonene reactions in indoor air under low, Atmos Env, pp.2008, 42(18)[DOI]
- Korea Occupational Safety, "Hazard identification of nanoparticles and prevention strategy for work related health problem", ~ (2007)
- Penttinen P, "Ultrafine particles in urban air and respiratory health among adult asthmatics", Eur Respir J, 17(3), pp.428~435 (2001)
- Donaldson K, "Current hypotheses on the mechanisms of toxicity of ultrafine particles", Ann Ist Super Sanita, 39(3), pp.405~410 (2003)
- Lee GW, "Exposure and risk assessment of size related heavy metals in particulate matter" (2009), Yonsei University
- Maeng SH, "The concepts of nanotoxicology and risk assessment of the nanoparticles", J Toxicol Pub Health, 21(2), pp.87~98 (2005)
- Harrison RM, "Measurement of number, mass and size distribution of particles in the atmosphere", Philos Transact A Math Phys Eng Sci, 358(1775), pp.2567~2580 (2000)
- Utell MJ, "Acute health effects of ambient air pollution: The ultrafine particle hypothesis", J Aerosol Med, 13(4), pp.355~359 (2000)
- Kreuter J, "Apolipoprotein- mediated transport of nanoparticle-bound drugs across the blood-brain barrier", J Drug Target, 10(4), pp.317~325 (2002)
- 박광식, "나노물질의 독성과 위해성평가 전략", 환경독성보건학회지, 20(4), pp.259~271 (2005), 환경독성보건학회
- 신동천, "극미세 입자의 인체 유해 영향에 대한 고찰", 한국실내환경학회지, 2(2), pp.81~88 (2006), 한국실내환경학회
- Maston U, "Indoor and outdoor concentrations of ultrafine particles in some Scandinavian rural and urban areas", Sci Total Environ, 343(1-3), pp.169~176 (2005)
- 김용식, "Indoor air quality for chemical and ultrafine particle contaminants from printers", Building and Environment, 42(5), pp.1949~1954, Pergamon Press Ltd.
- Lee CW, "Measurements of fine and ultrafine particles formation in photocopy centers in Taiwan", Atmos Env, 41(31), pp.6598~6609 (2007)
- Park JY, "Studies on nanoparticle events and seasonal variation nanoparticle concentration in the ambient atmosphere", The 2007 Environmental Societies Joint Conference, pp.1303~1305 (2007)
- Park KH, "Seasonal and diurnal cariations of ultrafine particle concentration in urban Gwangju, Korea: Observation of ultrafine particle events", Atmos Env, 42(4), pp.788~799 (2008)
- Choi MS, "Trace metals in airborne particulates collected at Cheju Island Korea", J KOSAE, 15(6), pp.727~738 (1999)
- Jeong JH, "Distribution characteristics of chemical composition of roadside airborne PM2.5 in Daejeon city", Proceedings of the 46th meeting of KOSAE, pp.547~548 (2008)
- Lee HM, "An assessment of the long-term concentration of heavy metals and associated risk in ambient PM10", J KOSAE, 12(5), pp.555~566 (1996)
- Chow JC., "Measurement methods to determine compliance with ambient air quality standards for suspended particle", J Air Waste Manag Assoc, 45(5), pp.320~382 (1995)
- Ministry of Labor, "A study on the revision of chemical substances exposure limit" (2005), hexavalent chrome
- Na DJ, "A study on the characteristics of PM10 and air-borne metallic elements produced in the industrial city", J KOSAE, 16(1), pp.23~35 (2000)
- Cho TJ, "A study on the size of ultrafine particles and heavy metal level in the atmosphere", pp.2010
- Cho EJ, "A study on the chemical commposition of atmospheric aerosols in Kwangju", pp.2001
- Kim SW., "Source characterization and concentration of chemical elements in fine particulate in an industrial area", pp.1997
- Koutrakis K, "Source apportionment of indoor aerosols in Suffolk and Onondaga Counties, New York", Environ Sci Technol, 26, pp.521~527 (1992)
