• 제목/요약/키워드: $PM_{2.5}$ fine particles

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저용량 PM2.5 도입부 개발 및 성능평가 (Design and Performance Evaluation of Low-Volume PM2.5 Inlet)

  • Kim Dae-Seong;Hong Sang-Beom;Lee Jae-Hun;Lee Gyu-Won
    • 한국대기환경학회:학술대회논문집
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    • 한국대기환경학회 2003년도 춘계학술대회 논문집
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    • pp.251-252
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    • 2003
  • Most particles capable of reaching the thoracic region of humans are in the size range below 10$\mu$m in diameter. Particles with a diameter smaller than 2.5 $\mu$m are deposited in large amounts in the alveolar region during mouth inhalation. The hazard caused by fine particles depends on their chemical composition and the site within the human respiratory system where they are deposited(Hinds, 1982). Therefore, the concentration of air borne fine particles is an important parameter for the evaluation of the degree of hazard in an atmospheric environment. (omitted)

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3-Stage DRUM 샘플러를 이용한 광주 도심지역의 봄철과 여름철 PM2.5 원소적 조성 비교 (Elemental Composition of PM2.5 Particulate with a 3-Stage DRUM Sampler during Spring and Summer Seasons in Urban Area of Gwangju, Korea)

  • 류성윤;김영준
    • 한국대기환경학회지
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    • 제21권6호
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    • pp.699-708
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    • 2005
  • To characterize the elemental composition of fine particles in urban area, $PM_{2.5}$ was collected by a 3-stage DRUM impactor at Gwangju during spring and summer. Time and size resolved concentrations for 19 trace elements were obtained by synchrotron X-Ray fluorescence analysis. Trace elements in summer were distributed in smaller size range compared to those in spring. Almost trace element concentrations in fine particles were highly increased during the Asian dust. In spring, soil elements such as Si, K, Ca, Ti and Fe had low enrichment factors indicating the dominant influence of soil dust. However, all elements had high enrichment factors in summer implying that these elements could be emitted from the anthropogenic sources. Factor analysis was conducted with the elemental composition data in order to identify anthropogenic sources of aerosols in urban area during spring and summer. Fine particles in spring have several sources such as soil dust originating from China continental region, coal and oil combustion, biomass burning, sea salt, ferrous and nonferrous metal sources. On the other hand, fine particles in summer were influenced by road dust, gasoline vehicle as well as coal and oil combustion, sea salt, ferrous and nonferrous metal sources.

2008년 동아시아 대륙으로부터 기원이 다른 먼지와 인위적 오염 입자의 광역적 이동 사례에 대한 분석 (An Analysis on the Episodes of Large-scale Transport of Natural Airborne Particles and Anthropogenically Affected Particles from Different Sources in the East Asian Continent in 2008)

  • 김학성;윤마병;손정주
    • 한국지구과학회지
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    • 제31권6호
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    • pp.600-607
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    • 2010
  • 2008년 동아시아 대륙에서 발생기원이 다른 먼지(황사)와 인위적 오염입자의 광역적 이동 사례를 NOAA위성 RGB 합성영상과 지상 입경별 분진(TSP, $PM_{10}$, $PM_{2.5}$)의 질량농도 관측으로 분석하였다. 또한 Terra/Aqua 위성 MODIS(Moderate resolution Imaging Spectroradiometer) 센서의 AOD(Aerosol Optical Depth)와 FW(Fine aerosol Weighting)를 통해 동아시아 지역에서 발생기원이 다른 대기 에어로졸의 분포와 입자 크기 특성을 분석하였다. 중국 북부와 몽골, 그리고 중국 황토고원에서 모래폭풍이 발생하여 광역적으로 이동하여 청원에 먼지입자(황사)로 영향을 주는 6 개의 사례분석을 실시하였다. 질량농도 TSP중 $PM_{10}$은 70%, $PM_{2.5}$는 16%로 조대입자(> $2.5\;{\mu}m$)의 비율이 큰 것은 사막과 반사막의 자연적 발생원에서 생성되었기 때문이다. 그러나, 모래 폭풍이 이동 과정에서 중국 동부의 산업 지역을 거쳐 유입하는 사례에서는 TSP 중 $PM_{2.5}$가 23%까지 증가하기도 했다. 중국 동부로부터 황해를 거쳐 한반도로 유입한 5개 다른 사례의 경우, TSP 중 $PM_{10}$, $PM_{2.5}$가 각각 82, 65%로 나타났다. 이와 같이 $PM_{2.5}$의 상대적 비율이 증가한 것은 인위적 오염입자의 영향 때문이다. 동아시아 지역에서 인위적 오염입자의 광역적 이동 사례에 대한 평균 AOD는 $0.42{\pm}0.17$로 황사에 의한 AOD($0.36{\pm}0.13$)와 비교하여 대기 에어로졸에 대한 비율이 높게 나타났다. 특히, 중국 동부에서 황해, 한반도, 동해에 이르는 광역적 지역에 AOD값이 높게 분포했다. 인위적 오염입자의 사례는 FW가 평균 $0.63{\pm}0.16$로 모래폭풍의 이동 사례의 $0.52{\pm}0.13$ 보다 높은 값을 보였다. 이는 대기 에어로졸에 대한 인위적 미세 오염 입자의 기여도가 클 수 있음을 제시하고 있다.

샘플유량과 기상조건에 따른 미세먼지 중량 측정용 기구간의 농도 비교 (Comparative Evaluation of Gravimetric Measurement Samplers for Fine Particles by Sampling Flow Rates and Meteorological Conditions)

  • 양원호;김대원;김진국;윤충식;허용;이부용
    • 한국환경과학회지
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    • 제14권1호
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    • pp.91-96
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    • 2005
  • Several samplers using gravimetric methods such as high-volume air sampler, MiniVol portable sampler, personal environmental monitor(PEM) and cyclone were applied to determine the concentrations of fine particles in atmospheric condition. Comparative evaluation between high-volume air sampler and Minivol portable sampler for $PM_{10}$, and between Minivol portable sampler and PEM was undertaken from June, 2003 to January 2004. Simultaneously, meteorological conditions such as wind speed, wind direction, relative humidity and temperature was measured to check the factors affecting the concentrations of fine particles. In addition, particle concen­trations by cyclone with an aerodynamic diameter of $4{\mu}m$ were measured. Correlation coefficient between high­volume air sampler and portable air sampler for $PM_{10}$ was 0.79 (p<0.001). However, the mean concentration for $PM_{10}$ by high-volume air sampler was significantly higher than that by Minivol portable sampler (p=0.018). Correlation coefficient between Minivol portable sampler and PEM for $PM_{2.5}$ as 0.74 (p<0.001), and the measured mean concentrations for $PM_{2.5}$ did not show significant difference. Difference of the measured con­centrations of fine particle might be explained by wind speed and humidity among meteorological conditions. Particle concentration differences by measurement samplers were proportional to the wind speed, but inversely proportional to the relative humidity, though it was not a significant correlation.

봄철 미세분진이 북경시 아동 폐기능에 미치는 급성영향에 관한 연구 (A Study on the Acute Effects of Eine Particles on Pulmonary Function of Schoolchildren in Beijing, China)

  • 김대선;유승도;차정훈;안승철;차준석
    • 한국환경보건학회지
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    • 제30권2호
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    • pp.140-148
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    • 2004
  • To evaluate the acute effects of fine particles on pulmonary function, a longitudinal study was conducted. This study was carried out for the schoolchildren (3rd and 6th grades) living in Beijing, China. Each child was provided with a mini-Wright peak flow meter and a preformatted health symptom diary for 40 days, and was trained on their proper use. Participants were instructed to perform the peak flow test three times in standing position, three times a day (9 am, 12 pm, and 8 pm), and to record all the readings along with the symptoms (cold, cough, and asthmatic symptoms) experienced on that day. Daily measurement of fine particles (PM$_{10}$ and PM$_{2.5}$) was obtained in the comer of the playground of the participating elementary school for the same period of this longitudinal study. The relationship between daily peak expiratory flow rate (PEFR) and fine particle levels was analyzed using a mixed linear regression models including gender, height, the presence of respiratory symptoms, and daily average temperature and relative humidity as extraneous variables. The total number of students participating in this longitudinal study was 87. The range of daily measured PEFR was 253-501$\ell$/min. In general, the PEFR measured in the morning was lower than the PEFR measured in the evening (or afternoon) on the same day. The daily mean concentrations of PM$_{10}$ and PM$_{2.5}$ over the study period were 180.2$\mu\textrm{g}$/㎥ and 103.2$\mu\textrm{g}$/㎥, respectively. The IQR (inter-quartile range) of PM$_{10}$ and PM$_{2.5}$ were 91.8$\mu\textrm{g}$/㎥ and 58.0$\mu\textrm{g}$/㎥. During the study period, the national ambient air quality standard of 150$\mu\textrm{g}$/㎥ (for PM$_{10}$) was exceeded in 23 days (57.5%). The analysis showed that an increase of 1$\mu\textrm{g}$/㎥ of PM$_{10}$ corresponded to 0.59$\mu\textrm{g}$/㎥ increment of PM$_{2.5}$. Daily mean PEFR was regressed with the 24-hour average PM$_{10}$ (or PM$_{2.5}$) levels, weather information such as air temperature and relative humidity, and individual characteristics including gender, height, and respiratory symptoms. The analysis showed that the increase of fine particle concentrations was negatively associated with the variability in PEFR. The IQR increments of PM$_{10}$ or PM$_{2.5}$ (at 1-day time lag) were also shown to be related with 1.54 $\ell$/min (95% Confidence intervals: 0.94-2.14) and 1.56$\ell$/min (95% CI: 0.95-2.16) decline in PEFR.R.ine in PEFR.ine in PEFR.

황사와 연무 시 PM10 및 PM2.5 미세먼지 조성 비교: 2010-2011년 고산지역 측정 (Composition comparison of PM10 and PM2.5 fine particulate matter for Asian dust and haze events of 2010-2011 at Gosan site in Jeju Island)

  • 김기주;이승훈;현동림;고희정;김원형;강창희
    • 분석과학
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    • 제27권1호
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    • pp.1-10
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    • 2014
  • 제주도 고산측정소에서 $PM_{10}$, $PM_{2.5}$ 미세먼지를 채취하여 주요 성분을 분석한 결과로부터 입경분포 및 오염 특성을 조사하였다. $NH{_4}{^+}$, nss-$SO{_4}^{2-}$, $K^+$, $CH_3COO^-$은 대체적으로 미세입자 분포하고, $NO{_3}{^-}$은 조대와 미세입자에 고루 분포하였으나 $Na^+$, $Cl^-$, $Mg^{2+}$, nss-$Ca^{2+}$은 대부분 조대입자에 분포되는 경향을 보였다. 황사 시에 조대입자와 미세입자에서 nss-$Ca^{2+}$이 36.7배, 15.0배 증가하고, $NO{_3}{^-}$은 조대입자에서 3.2배, 미세입자에서 3.1 배 높았다. 또 Al, Fe, Ca, K, Mg, Ti, Mn, Sr, Ba의 농도도 크게 증가하였다. 연무 시에는 nss-$SO{_4}^{2-}$, $NO{_3}{^-}$, $NH{_4}{^+}$ 농도가 조대입자에서 1.3~2.6배, 미세입자에서 1.5~4.2배 상승하였고, 특히 미세입자에서 $NO{_3}{^-}$ 농도가 크게 상승하였다. 고산지역 미세입자의 오염원 특성을 조사한 결과, 조대입자는 해염 영향이 가장 크고, 다음으로 토양, 인위적 오염원 순으로 영향을 많이 받았으나 미세입자는 인위적인 오염원 영향이 더 크고, 다음으로 해양과 토양 유입의 영향을 많이 받고 있는 것으로 나타났다.

춘천의 가정에서 미세분진 ($PM_{2.5}$)과 입자상 다환방향족탄화수소에 대한 계절적 노출 변동 (Seasonal Variations of Human Exposure to Residential Fine Particles ($PM_{2.5}$) and Particle-Associated Polycyclic Aromatic Hydrocarbons in Chuncheon)

  • 김희갑;정경미
    • Environmental Analysis Health and Toxicology
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    • 제21권1호
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    • pp.57-69
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    • 2006
  • Lately human exposure to fine particles smaller than $2.5{\mu}m$ in aerodynamic diameter ($PM_{2.5}$) has become a great concern in Korea due to their possible cause of elevated mortality, lung function decrements, and more frequent hospital admissions for asthma. This study was conducted to investigate seasonal variations of human exposure to residential $PM_{2.5}$ and particle-associated polycyclic aromatic hydrocarbons (PAHs). Ten homes in Chuncheon, Korea were visited for continuous 72 hour sampling of $PM_{2.5}$ in the living rooms using a MiniVol Portable Sampler from December 22, 2002 to November 3, 2003. During the same period, outdoor $PM_{2.5}$ samples were collected on the top of the Natural Sciences Building of Kangwon National University which is located in the middle of the ten households. Samples were analyzed for $PM_{2.5}$ mass concentrations and six selected PAHs. In two smoking homes, the highest $PM_{2.5}$ concentrations were measured ranging from 51.1 to 69.7 {\mu}g/m^3$ on average in all seasons, indicating smoking is a very important contributor to the elevation of indoor particle concentrations. Seasonal comparison showed that indoor particle concentrations were higher than outdoor ones except winter. Total PAH concentrations in smoking homes were highest in winter among the seasons primarily due to low ventilation rate, followed by the outdoor site and nonsmoking homes. BaP toxic equivalents (TEQs) were calculated for five PAHs. The TEQ for smoking homes in winter was highest followed by the outdoor site in winter. It is concluded that smoking and ventilation rate are two important contributors to the elevation of indoor $PM_{2.5}$ and PAH concentrations.