• Title/Summary/Keyword: 도로변 먼지

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Establishment of mobile roadside fine dust monitoring system (이동형 도로변 미세먼지 모니터링 시스템 구축)

  • Kim, Han-Na;Kim, Si-Eung;Kim, Hyeok-Jung
    • Proceedings of the Korean Society of Computer Information Conference
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    • 2021.07a
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    • pp.703-704
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    • 2021
  • 도로변에서 발생하는 미세먼지와 비산먼지는 인체에 각종 질병을 유발하는 발암물질로 알려져 있다. 본 논문에서는 효율적인 도로변 미세먼지의 농도를 측정을 위해 소형차량을 이용한 이동형 미세먼지 모니터링 시스템을 제안한다. 이 시스템은 기존의 대형차량의 운행으로 발행하는 미세먼지 사각지대를 해소하고, 고품질의 보급형 센서를 탑재하여 경제성을 제고한다. 또한, 미세먼지 측정 차량은 이동 중에도 실시간으로 측정가능하다. 이번 연구를 통해 미세먼지 측정 차량을 운행한 결과 도로변 상황을 즉각적으로 반영하는 결과를 나타내었다. 이러한 미세먼지 농도는 미세먼지 저감 및 관리를 위한 기초정보로 사용될 것을 기대한다.

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A Study on the Collection and Analysis of Tire and Road Wear Particles(TRWPs) as Fine Dust Generated on the Roadside (도로변에서 발생되는 미세먼지로써 타이어와 도로 마모입자 채집과 분석 연구)

  • Kang, Tae-Woo;Kim, Hyeok-Jung
    • Journal of the Korean Recycled Construction Resources Institute
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    • v.10 no.3
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    • pp.293-299
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    • 2022
  • Recently, various stakeholder are interested in microplastic to cause pollution of the marine's ecosystem and effort to conduct study of product's life cycle to reduce pollution of marine's ecosystem. The micorplastic refer to materials of the nano- to micro- sized units and it can be classified into primary and secondary. The primary microplastic mean the manufactured for use in the specific field such as the microbead of the cosmetic or cleanser. also, secondary mean the unintentionally generated during use of the product such as the textile crumb by the doing the laundry. Tire and Road Wear Particles(TRWPs) are also defined as secondary microplastic. Typically, TRWPs are created by friction between the tread compound's rubber of the tire and the surface of the road du ring the driving cars. Most of the generated TRWPs exist on the roadside and some of them were carried to marine by the rainwater. In this study, we perform the quantitative analysis of the TRWPs existed in fine dust at the roadside. So, we collected the dust from the roadside in Chungcheongnam-do's C site with a movement of 1,300 cars per the hour. The collected samples were separated according to size and density. And shape analysis was performed using the Scanning Electron Microscope(SEM). We were possible to discover a lot of TRWPs at the fine dust of the 100 ± 20 ㎛. And we analysis it u sing the Thermo Gravimetric Analysis(TGA) and Gas Chromatography/Mass Spectrometer(GC/MS) for the quantitative components from the tire. As a result, it was confirmed that TRWPs generated from the roadside fine dust were included the 0.21 %, and the tire and road components in the generated TRWPs consisted of the 3:7 ratio.

The Effect of the Green Space in Roadside and Building Height on the Mitigation of Concentration of Particulate Matters (가로녹지 및 건물 높이가 미세먼지 농도에 미치는 영향)

  • Hong, Suk-Hwan;Tian, Wanting;Ahn, Rosa
    • Korean Journal of Environment and Ecology
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    • v.34 no.5
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    • pp.466-482
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    • 2020
  • This study used 3D computational fluid dynamics (CFD) in the ENVI-met program to investigate how particulate matters (PM) generated on roads disperse through adjacent urban neighborhoods according to the urban development pattern. An urban area centered on a six-lane road in the vicinity of Miryang City Hall in Gyeongnam Province was selected to simulate the effect of the green space and building height on the PM concentration. The ENVI-met model considered the presence of green space and different building heights (high/low) on both sides of the road to examine the dispersion of PM. The result showed that the area of high-rise buildings and green space had the lowest PM concentration dispersed to the adjacent area, followed by the area of high-rise buildings and no green space. In contrast, the PM concentration remained relatively high for low-rise buildings, regardless of the green space. The reason for the low PM concentration in the area with high-rise buildings was a strong building wind, which caused PM to disperse to the outside, lowering the PM concentration quickly. These results indicate that the PM can disperse faster, and the PM concentration remains low in the urban neighborhood. On the other hand, green space had no significant effect on reducing PM in the urban neighborhood. In particular, when there are low-rise buildings on both sides of the road, the green space has no effect on the PM concentration in the urban neighborhood. Since this study considered only the case of PM emitted from the road, future studies should investigate other factors to figure out the dispersion model of PM and conduct on-site experiments.

Establishment of a mobile monitoring system for roadside fine dust vulnerable point (이동형 도로변 미세먼지 취약지점 모니터링 시스템 구축)

  • Kim, Hyeok-Jung;Kang, Min-Ji;Kim, Han-Na
    • Proceedings of the Korean Society of Computer Information Conference
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    • 2022.07a
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    • pp.685-686
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    • 2022
  • 미세먼지는 인체에 직·간접적인 질병을 유발하는 1급 발암물질로 알려져 있다. 본 논문에서는 도로변에서 발생 되는 미세먼지 및 미세먼지 전구체 농도를 측정을 위한 이동형 미세먼지 모니터링 시스템을 제안한다. 이 시스템은 기존의 대형차량 대비 미세먼지 측정 사각지대를 해소하고, 성능등급 1등급 장비 및 온습도 보정 모듈 장착으로 결과의 높은 정확도를 확보하였다, 또한, 개발된 데이터 표출 시스템을 통해 미세먼지 측정 차량을 운행한 결과를 웹사이트에서 실시간 확인 가능하도록 하였다. 이동형 미세먼지 측정 차량 운영을 통해 얻어진 정보는 보행자를 위한 정보 제공 및 미세먼지 저감 및 관리를 위한 정책 마련의 기초정보로 사용될 것을 기대한다.

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Distribution Characteristics of Platinum Group Elements in Roadside Dust from Daejeon, Korea (대전 도로변 먼지내 Platinum Group Elements의 분포 특성)

  • Lim, Jong-Myoung;Jeong, Jin-Hee;Lee, Jin-Hong
    • Journal of Environmental Impact Assessment
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    • v.27 no.5
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    • pp.405-416
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    • 2018
  • In this research, the distribution of Platinum Group Elements (PGEs) at roadside dust in Daejeon, Korea was examined using an ICP-MS (Inductively Coupled Plasma-Mass Spectrometry) technique. For the quality assurance of the determination, method validation based on its accuracy and precision was conducted using SRM (Standard Reference Material). It was found that the relative errors of Pt, Pd, and Rh against each SRM value were -0.7%, -10.0%, and -20.4%, respectively, while relative standard deviations for three elements were less than 10%. The concentrations of Pt, Pd and Rh in roadside dust averaged as $17.4{\pm}9.2{\mu}g/kg$, $283.6{\pm}20.5{\mu}g/kg$, and $7.3{\pm}2.8{\mu}g/kg$, respectively. The concentrations of Pt and Rh have significantly higher distribution patterns in the dust at roadside and underground parking lot than those in soil of the background or other urban area. The correlation analysis between concentrations of PGEs in roadside dust indicates that the distribution of Pt and Rh concentration were strongly affected by automobile sources.

An Experimental Study on Fine Dust Emissions near Special Modified Asphalt Pavement and Conventional Asphalt Pavement (특수개질 및 일반 아스팔트 포장체 도로변의 미세먼지 발생에 대한 실험적 연구)

  • Tae-Woo Kang;Hyeok-Jung Kim
    • Journal of the Korean Recycled Construction Resources Institute
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    • v.11 no.3
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    • pp.282-288
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    • 2023
  • In this study, we analyzed the amount of roadside fine dust generated from newly constructed specially modified asphalt pavement and general asphalt pavement from existing roads. We collected the 1,000 g (100 g/day) of dust samples from the roadside of the express bus terminal and commercial facility area in Chungcheongnam-do's C site at three-day intervals during the summer of 2022 and 2023. The collected samples were separated from fine dust according to size in the 75-150 ㎛ range and, were separated only from Tire and Road Wear Particles through density separation. No.1-3 are general asphalt pavement section as an existing road. Fine dust and Tire and Road Wear Particles in No.1-3 were 24.27 g, 24.36 g, 0.53 g, and 0.53 g, respectively, and the quantitative results for 2022 and 2023 were similar. On the other hand, No.4-6 are newly constructed specially modified asphalt pavement section. Fine dust decreased by 14.8 % and tire and road wear particles decreased by 29.6 % in 2023 compared to 2022 in No.4-6. In addition, according to the results of thermogravimetric analysis, Tire and road wear particles in No.1-3 are tire and road components at 30 % and 70 %, respectively. And Tire and road wear particles in No.4-6 are tire and road components at 35 % and 65 % in 2023, respectively. From these results, it was confirmed that the newly constructed specially modified asphalt pavement can be effective in reducing roadside fine dust and Tire and Road Wear Particles. However, there may be some shortcomings in conclusive research results due to limited space and sample collection period. In the future, we plan to conduct various case studies.

Mitigation Effect on Airborne Particulate Matter Concentration by Roadside Green Space Type and Impact of Wind Speed (도로변 녹지 유형별 미세먼지 농도 저감 효과와 이에 대한 풍속의 영향 연구)

  • Tae-Young Choi;Da-In Kang;Jaegyu Cha
    • Journal of Environmental Impact Assessment
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    • v.32 no.6
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    • pp.437-449
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    • 2023
  • This study measured PM10 concentrations and wind speeds in buffer green spaces and neighborhood parks located along the road, and compared them with roadside measurementresults to understand the effect of mitigating PM10 concentrations by type of green space and the influence of wind speeds on it. As a result of the analysis, the effect of mitigating PM10 concentration was different depending on the type of roadside green space, and an increase in wind speed had a significant effect on reducing PM10 concentration. In buffer green areas with high planting density, wind speed was low and PM10 stagnated inside, resulting in the highest concentration. On the other hand, green areas in neighborhood parks with relatively low planting density had high wind speeds and the lowest PM10 concentration. The non-green area within the neighborhood park recorded the highest wind speed, which was advantageous for the spread of PM10, but the concentration was higherthan that of the green area. Therefore, in orderto reduce PM10 concentration in roadside green space, it is necessary to create green space with good ventilation, and the combined effect of green space and wind speed seems to be more advantageous in reducing PM10 concentration. Green spaces capture and remove PM inside, contributing to reducing the concentration of PM outside. In order to manage PM in the entire city and on roads, it is necessary to increase planting density and leaf area in roadside green spaces, such as buffer green spaces, so that PM can be removed within the green spaces. However, in green spaces such as neighborhood parks that are actively used by city residents, in orderto minimize damage to users due to PM, it is desirable to create green spaces with a structure that allows PM to spread to the outside rather than stagnate inside.

Study on the Impact of Roadside Forests on Particulate Matter between Road and Public Openspace in front of Building Site - Case of Openspace of Busan City hall in Korea - (도심 도로변 가로녹지가 주변 오픈스페이스의 미세먼지농도에 미치는 영향 연구 - 부산시청 광장을 대상으로 -)

  • Hong, Suk-Hwan;Kang, Rae-Yeol;An, Mi-Yeon;Kim, Ji-Suk;Jung, Eun-Sang
    • Korean Journal of Environment and Ecology
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    • v.32 no.3
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    • pp.323-331
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    • 2018
  • This study was conducted to examine the effects of constructing streetside urban forests on particulate matter (PM) content in pedestrian paths and open spaces created between the main streets and buildings in a high-rise, high-density urban area. The study site is a 70m-wide open space between Busan City Hall and Jungang-street in Busan, Korea. The results showed that the density of PM differences between the open space and the adjacent main street were small in regions without linear trees and shrub rows during both the weekdays and weekend. On the other hand, the areas with linear trees and shrub rows were found to have significantly higher concentrations of PM compared to the roadway. In particular, sections with linear trees and shrub rows had higher PM levels both on roads and in adjacent open space, indicating that the composition of linear trees and shrub rows increased the concentration of PM in the off-street open space in areas with wide space between the roadway and building. The impact was more significant in the open space than the roadway. This phenomenon can be explained by the fact that PM generated by vehicles flows through the roadside shrubs by rapid wind flow but does not disperse widely in the pedestrian paths where the wind flow was reduced. In this study, we found that the roadside tree and shrub walls slowed the flow of wind, causing vehicle-emitted PM to accumulate if a wide open space was created between the road and building, resulting in higher concentration of PM in the open space. We confirmed that the distance between the road and building was a critical factor for constructing linear trees and shrub rows to reduce PM generated by vehicle traffic.