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도로변 공원의 공간조성유형에 따른 초미세먼지 분포 특성 - 부산시 송상현광장을 사례로-

Characteristics of Particulate Matter 2.5 by Type of Space of Urban Park - Focusing on the Songsanghyeon Plaza in Busan -

  • 안로사 (부산대학교 대학원 조경학과) ;
  • 홍석환 (부산대학교 조경학과)
  • Ahn, Rosa (Dept. of Landscape Architecture, Pusan National University) ;
  • Hong, Sukhwan (Dept. of Landscape Architecture, Pusan National University)
  • 투고 : 2021.11.08
  • 심사 : 2021.12.06
  • 발행 : 2021.12.31

초록

본 연구는 도심 내 주요 초미세먼지(PM2.5) 발생원인 도로 인근에 조성된 도시공원을 대상으로 도시공원 내부 공간조성유형에 따라 PM2.5의 농도변화를 분석하여 특성을 살펴보고자 하였다. 연구대상지는 부산시 진구 도심 내 12차선의 도로 중심부에 광장형 공원형태로 조성된 송상현광장으로 선정하였으며, 공원의 공간조성유형은 토지피복유형과 식생구조에 따라 도로변 광장(A), 선큰광장(B), 도로 경계부 다층식재지(C), 교목 하부(D), 잔디광장(E)으로 총 5가지로 구분하였다. PM2.5는 초미세먼지 등급별 국가예보에 따라 좋음일, 보통일, 나쁨일 3일씩 총 9회 측정한 결과를 바탕으로 평균비교 분석을 수행하였다. PM2.5 좋음일 기준으로 송상현광장 내 공간조성유형별 농도는 D, E < B, C < A 순으로 통계적 유의성이 있었다. PM2.5 보통일과 나쁨일 기준은 D, E < A, B, C 순으로 유의하였다. 공간조성유형별 송상현광장 내 PM2.5 농도 특성은 인근 차도로부터 확산되는 PM2.5의 대기의 흐름의 영향이 큰 것으로 판단되었다. 차도와 15m 거리에 위치해 있는 A와 C의 경우 PM2.5 농도가 높았으나, B는 도로로부터 40m 거리에 떨어져 있는 PM2.5 농도가 높았다. 이는 B는 외벽구조로 둘러싸여 공간 내부의 공기순환이 느려 상대적으로 대기가 확산되지 못하는 것으로 판단되었다. D와 E의 경우 C의 공간조성유형을 통해 대기의 흐름이 차단된 후 공원 내부에서 대기의 흐름이 원활한 구조여서 PM2.5 농도가 상대적으로 낮은 것으로 판단하였다.

Roadside pollution has been identified as the main cause of PM2.5 in urban areas. Green infrastructure has been understood to mitigate air pollution from roadside traffic effectively, but complication depend on environmental variables. This study aimed to investigate the characteristic of PM2.5 by the type of space in an urban park located in Songsanghyeon Plaza, surrounded by a 12-lane road on all sides. Type of space was typically classified as roadside square (A), sunken square (B), a mix of trees and hedges/shrubs (C), trees only (D), and grass square (E) according to the land-use type and layers of trees. PM2.5 was measured for nine days, three days for three different Air Quality Forecasts-Good level (0~15㎍/m3), Moderate level (16~35㎍/m3), and Unhealthy level (36~75㎍/m3). The analysis result was as follows. At good levels, there was statistical significance in the order of D, E < B, C < A. In the case of moderate levels and unhealthy levels, D and E were statistically lower than other land-use types. The characteristic of PM2.5 in the urban park by type of space was affected by atmospheric flow into the road. The relatively high concentration of A and C was located near the roads. Although B was far away from the road, the reason for the high concentration of PM2.5 was that no structures blocked the air pollution. Thanks to the type of space C, filtering the air pollution from the roads, the concentration of PM2.5 in D and E was relatively low.

키워드

과제정보

이 논문은 한국연구재단에서 지원하는 연구비(NO. 2019R1F1A1053911)에 의하여 연구되었으며, 안로사의 석사학위논문을 수정·보완하여 작성되었음.

참고문헌

  1. Abhijith, K. V., P. Kumar, J. Gallagher, A. McNabola, R. Baldauf, F. Pilla, B. Broderick, S. Di Sabatino and B. Pulvirenti(2017) Air pollution abatement performances of green infrastructure in open road and built-up street canyon environments-A review. Atmospheric Environment 162:71-86. https://doi.org/10.1016/j.atmosenv.2017.05.014
  2. Brimblecombe, P. and Y. Xing(2019) Role of vegetation in deposition and dispersion of air pollution in urban parks. Atmospheric Environment 201: 73-83. https://doi.org/10.1016/j.atmosenv.2018.12.027
  3. Chae, H. J.(2009) Effect on the PM10 concentration by wind velocity and wind direction. Journal of Environmental and Sanitary Engineering 24(3): 28-45.
  4. Choi, T. Y., D. I. Kang and J. G. Cha(2019) An analysis of the correlation between seoul's monthly particulate matter concentrations and surrounding land cover categories. Korean Society of Environmental Impact Assessment 28(6): 568-579.
  5. City of Busan(2020) Results of the 2019 Busan Metropolitan City Traffic Survey (I) Vehicle Traffic Survey. (in Korean).
  6. Curtis, L., W. Rea, P. Smith-Willis, E. Fenyves and Y. Panc(2006) Adverse health effects of outdoor air pollutants. Environment International 32(6): 815-830. https://doi.org/10.1016/j.envint.2006.03.012
  7. Donaldson, K. and W. MacNee(2001) Potential mechanism of adverse pulmonary and cardiovascular effects of particulate air pollution(PM10). International Journal of Hygiene and Environmental Health 203(5-6): 411-415. https://doi.org/10.1078/1438-4639-00059
  8. Evans, J., A. Donkelaar, R. V. Martin, R. Burnett, D. G. Rainham, N. J. Brikett, and D. Krewski(2013) Estimates of global mortality attributable to particulate air pollution using satellite imagery. Environmental Research 120: 33-42. https://doi.org/10.1016/j.envres.2012.08.005
  9. Han S. H.(2012) A Study on the Emissions and Chemical Characteristic of Resuspended Dust from Paved Roads in Urban Areas. Ph.D. Thesis, Inha University Graduate School. Korea.
  10. Han, D., H. Shen, W. Duan and L. Chen(2020) A review on particulate matter removal capacity by urban forests at different scales. Urban Forestry and Urban Greening. 48. 126565. https://doi.org/10.1016/j.ufug.2019.126565
  11. Hwang, K. I., B. H. Han, J. I. Kwark and S. C. Park(2018) A study on decreasing effects of ultra-fine particles (pm2.5) by structures in a roadside buffer green - a buffer green in Songpa-gu, Seoul -. Korean Institute of Landscape Architecture 46(4):61-75.
  12. Hong, S. H., R. Y. Kang, M. Y. An, J. S. Kim, and E. S. Jung(2018) 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-. Korean Journal of Environment and Ecology 32(3): 323-331. https://doi.org/10.13047/KJEE.2018.32.3.323
  13. Janhall, S.(2015) Review on urban vegetation and particle air pollution. deposition and dispersion. Atmos. Environ. 105: 130-137. https://doi.org/10.1016/j.atmosenv.2015.01.052
  14. Jeon, B. L. and Y. S. Hwang(2010) Chemical properties of the metallic elements and the mass concentration of PM10 and PM2.5 observed in Busan, Korea in springtime of 2006-2008. Journal of Korean Earth Science Society 31(3): 214-245. https://doi.org/10.5467/JKESS.2010.31.3.214
  15. Jeon, B. L.(2015). Characteristics of the springtime weekday/weekend on mass and metallic elements concentrations of PM10 and PM2.5 in Busan. Journal of Environmental Science International 24(6): 777-784. https://doi.org/10.5322/JESI.2015.24.6.777
  16. Keeler, G. J., M. Morishita and L. H. Young(2005) Characterization of complex mixtures in urban atmospheres for inhalation exposure studies. Experimental and Toxicologic Pathology 57(1): 19-29. https://doi.org/10.1016/j.etp.2005.05.021
  17. Kim, B.(2020) Risk Perception and Satisfaction in Outdoor Activities Related to Particulate Matter : Focused on Bikers. Ph.D. Thesis, Graduate School of Environmental Studies. Korea.
  18. Kim, I. (2021). Analysis of the effect of reducing air pollution in parks created in cities. domestic and international IP analysis reports. Ministry of Environment, Korea Environmental Industry and Technology Institute. (in Korean)
  19. Koo, M. A.(2019) The relationship between particular matter reduction and space shielding rate in urban neighborhood park. Korean Institute of Landscape Architecture 47(6): 66-77. https://doi.org/10.9715/KILA.2019.47.5.066
  20. Kumar, P. and K. V. Abhijith(2019) Field investigations for evaluating green infrastructure effects on air quality in open-road conditions. Atmospheric Environment 201: 132-147. https://doi.org/10.1016/j.atmosenv.2018.12.036
  21. Lee, H. Y. and N. J. Kim(2017) The impact of fine particular matter risk perception on the outdoor behavior of recreationists: An application of the extended theory of planned behavior. The Tourism Sciences Society of Korea 41(7): 22-44.
  22. Lee, Y. K., H. S. Lim, S. M. Hong, C. H. Oh, K. J. Lee and J. S. Lee(2012) Regional characteristics of particle size distribution of PM10. Journal of Korean Society for Atmospheric Environment 28(6): 666-674. https://doi.org/10.5572/KOSAE.2012.28.6.666
  23. National Assembly Budget Office(2019). Analysis of Fine Dust Response Projects.(in Korean)
  24. National Institute of Environmental Research(2018). Ultra Fine Dust Measuring Device Guide Book. Ministry of Environment. (in Korean)
  25. National Institute of Forest Science(2019). Urban Forest Guidelines for the Creation and Management of New Projects(reduction of fine dust) in 2019. Korea Forest Service.(in Korean)
  26. Park, C. S. (2017). Variations of PM10 concentration in Seoul during 2015 and relationships to weather condition. Journal of the Association of Korean Photo-Geographers 27(2): 47-64. https://doi.org/10.35149/jakpg.2017.27.2.004
  27. Park, G. H., J. W. Jeong and J. G. Cho(2012) Evaluation of pollution characteristics and chemical composition of PM2.5 in the ambient air of Busan(III). The Annual Report of Busan Metropolitan city Institute of Health & Environment 22(1): 142-159.
  28. Park, S. A., H. Y. Kong, S. H. Kim, S. Park and Y. K. Shin(2016)Characteristics of thermal variations with the different land covers in an urban area. Ecology and Resilient Infrastructure 3(1): 46-53. https://doi.org/10.17820/eri.2016.3.1.046
  29. Seo, M. and H. C. Cho(2017) The effect of PM10 and PM2.5 on life satisfaction: Focusing on WTP. Environmental and Resource Economics Review 26(3): 417-449. https://doi.org/10.15266/KEREA.2017.26.3.417
  30. Sung, S. Y.(2019) Environmental planning countermeasures considering spatial distribution and potential factors of particulate matters concentration. Journal of the Korea Society of Environmental Restoration Technology 23(1): 89-96. https://doi.org/10.13087/KOSERT.2019.23.1.89
  31. The Government of the Republic of Korea(2019) The 5th Comprehensive National Land Plan. (2020-2040). Cooperation with related ministries. (in Korean)
  32. Yeo, M. J. and Y. P. Kim(2020) Trends of the PM10 concentrations and high PM10 concentration cases in Korea. Journal of Korean Society for Atmospheric Environment 35(2): 249-264. https://doi.org/10.5572/kosae.2019.35.2.249