• The Influence of Land Use on the Concentration Levels and Distribution Characteristics of Polycyclic Aromatic Hydrocarbons (PAHs) in Korea
  • Noh, Hoe-Jung;Yoon, Jeong Ki;Yun, Dae-Geun;Yu, Soon-Ju;Kim, Tae Seung;Lee, Jai-Young;
  • National Institute of Environmental Research;National Institute of Environmental Research;Green Environment Centers Association;National Institute of Environmental Research;National Institute of Environmental Research;School of Environmental Engineering, University of Seoul;
  • 국내 토지이용도별 토양 중 다환방향족탄화수소류(PAHs)의 농도 수준 및 분포 특성
  • 노회정;윤정기;윤대근;유순주;김태승;이재영;
  • 국립환경과학원;국립환경과학원;녹색환경지원센터연합회;국립환경과학원;국립환경과학원;서울시립대학교 환경공학부;
Abstract
We investigated soil contamination depending on the land use by examining the contamination levels and distribution characteristics of 16 polycyclic aromatic hydrocarbons (PAHs) in the national soil. Total PAHs (the sum of 16 PAH concentrations) and carcinogenic PAHs (the sum of seven carcinogenic PAH concentrations) were $8.50{\sim}3,437.16{\mu}g/kg$ and $2.94{\sim}2,136.96{\mu}g/kg$, respectively. The concentration of benzo(a)pyrene, one of the contaminants regulated by the soil quality standard in the nation, was $ND{\sim}924.73{\mu}g/kg$. Its maximum value of $924.73{\mu}g/kg$ was detected in railroad (Region 3) and is approximately 13% of the standard value for Region 3 (i.e., 7 mg/kg). We also investigated the characteristics of contamination sources of PAHs in soil of the upland, forests, roads, and railroads, examining the fraction distribution of PAHs concentration by the number of benzene rings against the total PAHs concentration. The results demonstrate that the mean fraction of 4~6-ring PAHs against total PAHs concentration in soil was in the range of 51.8~80.7% with relative abundance of high-molecular PAHs, showing that the origin of contamination is under the category of combustion sources. When the molecular indices (Flu/(Flu/Pyr), Ant/(Ant+Phe), InP/(InP+BP), and BaA/(BaA+Chr)) were applied, they were also categorized as petroleum-based combustion sources. The individual PAH concentrations in soil by the land use were grouped into Regions 1, 2, and 3, which are statistically treated and are the parts of the national category system of soil quality standard. As a result, the concentration level of 16 PAHs was $0.02{\sim}2.63{\mu}g/kg$ in Region 1, $0.05{\sim}4.26{\mu}g/kg$ in Region 2, and $2.36{\sim}178.27{\mu}g/kg$ in Region 3. The concentration level of 6 carcinogenic PAHs was 14.2~320.4% against that of benzo(a)pyrene in Region 3 and sites of recycling waste sleepers. Considering that there were similarities among PAHs in terms of structures and toxicities, it would be recommended to review other types of carcinogenic PAHs together with benzo(a)pyrene when developing the soil quality standards in the nation.

Keywords: PAHs;Soil;Land use;Contamination sources;

References
  • 1. Aryal, R.K., Furumai, H., Nakajima, F., and Boller, M., 2006, Characteristics of particle-associated PAHs in a first flush of a highway runoff, Water Sci. Technol., 53, 245-251.
  •  
  • 2. Butler, J.D., Butterworth, V., Kellow, S.C., and Robinson, H.G., 1984, Some observations on the polycyclic aromatic hydrocarbon(PAH) content of surface soils in urban areas, Sci. Total Environ., 33, 75-85.
  •  
  • 3. Cho, K.-C., Whoang, K.-C., Lim, C.-S., Cho, K.-R., and Kim, H.-K., 1996, Concentrations and distributions of PAHs in soils sampled at the roadsides in Seoul, J. Kor. Air Poll. Res. Assoc., 12(5), 517-521.
  •  
  • 4. Chung, David, Yoon, J.-I., Kim, M.-S., Yu, H.Y., Im, J.-H., Kim, Y.-J., Park, H.-Y., Cho, J.-H., Kim, K.-K., Han, S.-O., Shin, S.-K., and Oh, G.-J., 2012, Hazardous characteristics of waste timber from rail road, J. Kor. Soc. Waste Manage., 29(1), 59-69.
  •  
  • 5. Dong, T.T. and Lee, B.-K., 2009, Characteristic, toxicity, and source apportionment of polycyclic aromatic hydrocarbons (PAHs) in road dust of Ulsan, Korea, Chemosphere, 74, 1245-1253.
  •  
  • 6. Florida Department of Environmental Protection (FDEP), 2012, Guidance for comparing background and site chemical concentrations in soil.
  •  
  • 7. International Programme on Chemical Safety (IPCS), 1998, Environmental Health Criteria 202, Selected Non-Heterocyclic Polycyclic Aromatic Hydrocarbons.
  •  
  • 8. Jiang, Y.-F., Wang, X.-T., Wang, F., Jia, Y., Wu, M.-H., Sheng, G.-Y., and Fu, J.-M., 2009, Levels, composition profiles and sources of plycyclci aromatic hydrocarbons in urban soil of Shanghai, China, Chemosphere, 75, 1112-1118.
  •  
  • 9. Jin, Y.-K., Lee, M.-G., and Kam, S.-K., 2006, Distribution characteristics of polycyclic aromatic hydrocarbons (PAHs) in soils in Jeju City of Jeju Island, Korea, J. Environ. Sci., 15(5), 405-415.
  •  
  • 10. Kim, D.-H., Kim, S.-J., Kim, Y.-K., Kim, S.-Y., Ok, S.-B., and Ok, G., 2001, Distribution characteristics of PCDDs/DFs and polycyclic aromatic hydrocarbons in soil at Daegu City, J. Kor. Soc. Environ. Anal., 4(1), 23-28.
  •  
  • 11. Kim, D.-H. and Ok, G., 2005, Survey on concentration characteristics of polycyclic aromatic hydrocarbons in soil in Seoul, Environ. Sci., 14(1), 71-80.
  •  
  • 12. Kim, S.-J., Chung, Y.-H., and Ok, G., 2000, Concentration levels and distribution characteristics of polycyclic aromatic hydrocarbons (PAHs) at soil in Changwon City, J. Kor. Soc. Environ. Anal., 3(3), 171-175.
  •  
  • 13. Lee, J.-S. and Park, J.-Y., 2010, Wood properties and residual creosote oil of disused railway wood ties, J. Agric. Sci., 37(3), 465-469.
  •  
  • 14. Lim, J.S., Kim, S.S., Park, D.S., Joo, J.H., Lim, C.K., and Heo, J.H., 2007, Monitoring of polycyclic aromatic hydrocarbon residues in environmental samples in Korea, Kor. J. Pestic. Sci., 11(2), 95-105.
  •  
  • 15. Maliszewska-Kordybach, B., Smreczak, B., Klimkowicz-Pawlas, A., and Terelak, H., 2008, Monitoring of the total content of polycyclic aromatic hydrocarbons (PAHs) in arable soils in Poland, Chemosphere, 73, 1284-1291.
  •  
  • 16. Ministry of Environment (MOE), 2009a, Soil Environment Conservation Act.
  •  
  • 17. Ministry of Environment (MOE), 2009b, Soil official testing method.
  •  
  • 18. Nam, J.J., Hong, S.-Y., Lee, J.-S., So, K.-H., and Lee, S.-H., 2007, Polycyclic aromatic hydrocarbons (PAHs) in Korean Soil: Distribution by Depth and Land Use, J. Environ. Toxicol., 22(2), 129-135.
  •  
  • 19. Nam, J.J., Song, B.H., Eom, K.C., Lee, S.H., and Smith, A., 2003, Distribution of polycyclic aromatic hydrocarbons in agricultural soils in South Korea, Chemosphere, 50, 1281-1289.
  •  
  • 20. Nam, J.J., Thomas, G.O., Jaward, F.M., Steinnes, E., Gustafsson, O., and Jones, K.C., 2008, PAHs in background soils from Western Europe: Influence of atmospheric deposition and soil organic matter, Chemosphere, 70, 1596-1602.
  •  
  • 21. National Institute of Environment Research (NIER), 2007, Establishment of the soil quality standards for organic pollutants (II).
  •  
  • 22. National Institute of Environment Research (NIER), 2009, Assessment for characteristic of POPs contamination in soil.
  •  
  • 23. USEPA, 1993, Provisional Guidance for Quantitative Risk Assessment of Polycyclic Aromatic Hydrocarbons, Office of Research and Development, EPA/600/R-93/089.
  •  
  • 24. USEPA, 1996, Soil Screening Guidance: User's Guide, Office of Emergency and Remedial Response, Washington, DC, EPA/540/R-96/018.
  •  
  • 25. Vogt, N.B., Brakstad, F., Thrane, K., Nordenson, S., Krane, J., Aamot, E., Kolset, K., Esbensen, K., and Steinnes, E., 1987, Polycyclic aromatic hydrocarbons in soil and air: Statistical analysis and classification by the SIMCA method, Environ. Sci. Technol., 21, 35-44.
  •  
  • 26. WHO, 2004, Coal tar creosote.
  •  
  • 27. Yunker, M.B., Macdonald, R.K, Vingarzan, R., Mitchell, R.H., Goyette, D., and Sylvestre, S., 2002, PAHs in the Fraser River Basin: a critical appraisal of PAH ratios as indicators of PAH source and composition, Org. Geochem., 33, 489-515.
  •  

This Article

  • 2014; 19(6): 59-71

    Published on Dec 31, 2014

  • 10.7857/JSGE.2014.19.6.059
  • Received on Sep 18, 2014
  • Revised on Dec 6, 2014
  • Accepted on Dec 19, 2014