Document Type : Original Article

Authors

1 PhD student of Sedimentology, Department of Geology, North Tehran Branch, Islamic Azad University, Tehran, Iran

2 Associate professor, Department of Geology, North Tehran Branch, Islamic Azad University, Tehran, Iran

3 Associate professor, Agricultural Research, Education and Extension Organization, Soil Conservation and Watershed Management Research Institute, Tehran, Iran

4 Assistant professor, Department of Geology, North Tehran Branch, Islamic Azad University, Tehran, Iran

Abstract

Introduction: Polycyclic aromatic hydrocarbons (PAHs) are introduced into the environment by human activities and are deposited in the river bed. These compounds are among environmental pollutants and are extremely harmful to human health and other living things even in very small amounts. For this reason, determining the concentration of these pollutants is very important to evaluate the quality of river water. About a hundred compounds of PAHs that have been identified by the Environmental Protection Agency. They have 16 major harmful and pathogenic compounds, and for this reason, they have been introduced as pioneering pollutants. For this purpose, in the present study, the concentrations of PAHs were determined in the Karun River.
Materials and Methods: In this study, 19 samples of PAHs were collected along the Karun River from Cham Golak in the north of Khuzestan to Choibedeh in the south of Khuzestan in 2022. The collected samples were immediately stored in glass bags at a temperature of -10°C and transported to the laboratory. Until the time of extraction, the samples were dried in a freeze dryer and then kept in a freezer at -50°C. Before the extraction operation, all the samples were powdered and passed through a sieve with mesh less than 0.63. After determining the amounts of each of the desired PAHs, using Dionex™ ASE™ 3, it was determined whether the PAHs has fuel or petroleum origin. Finally, the concentrations of the obtained PAHs were compared with the American Sediment quality guidelines. In this standard, two risk categories, ERL and ERM, are considered for sediment pollution.
Results: Based on the average concentration of studied PAHs, Benzo (b) fluoranthene and phenanthrene were the most polluted in proportion to concentration among all studied PAHs. The concentration of Benzo (k) fluoranthene, Fluorene, Pyrene and Indeno (1,2,3-c,d) pyrene was also more than 1 μg.kg-1 of sediment, which was high compared to the average concentration of other PAHs. Other PAHs had an average concentration of less than 0.80 μg.kg-1. The minimum concentration of hydrocarbons varied between 0.01-2.15 μg.kg-1 and their maximum concentration between 0.05-8.97 μg.kg-1 of sediment. The results of skewness (-0.75<SKW<3.0) showed that there were many spatial variations for all pollutants, but Anthracene with a skewness of 0.3 has the most spatial changes, with the highest concentration in the south of the Karun River, and Benzo (b) fluoranthene has the skewness equal to -0.75, then, the highest pollutant concentration was in the north of Karun River. Except for the four hydrocarbons Benzo (b) fluoranthene, Benzo (k) fluoranthene, Indeno (1,2,3-c,d) pyrene and Benzo (g,h,i) perylene, the concentration of the other pollutants in the Karun River is lower than the Sediment Management Standard (SQS) limits ( Discussion: The origin of the pollutant’s evaluation showed that in the north of the Karun River, there was more fuel pollution, but in the center and south of this river, both fuel and oil sources were observed. These results showed that air pollution had a greater effect on increasing the concentration of hydrocarbons in the sediments of this river. In addition, the fuel of boats in the Ahvaz to Abadan area can be an important factor in increasing PAHs pollution with fuel origin. Therefore, although PAHs pollution was observed in this river, it was not at a critical level in terms of concentration.

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  1. Bateni, F., Mehdinia, A. and Seyed Hashtroudi, M., 2019. Ecological risk assessment of polycyclic aromatic hydrocarbons in the Persian Gulf surface sediments, Bushehr. Iranian Journal of Health and Environment, 11 (4): 563-574. (in Persian).
  2. Baumard, P., Budzinski, H., Garrigues, P., Sorbe, J.C., Burgeot, T. and Bellocq, J., 1998. Concentrations of PAHs (polycyclic aromatic hydrocarbons) in various marine organisms in relation to those in sediments and to trophic level. Marine Pollution Bulletin 36: 951–960.
  3. Brewster, C.S., Sharma, V.K., Cizmas, L. and McDonald, T.J., 2018. Occurrence, distribution and composition of aliphatic and polycyclic aromatic hydrocarbons in sediment cores from the Lower Fox River, Wisconsin, US. Environmental Science and Pollution Research, 25(5): 4974-4988.
  4. Kamal, A., Malik, R.N., Martellini, T. and Cincinelli, A., 2014. Cancer risk evaluation of brick kiln workers exposed to dust bound PAHs in Punjab province (Pakistan). Science of the Total Environment. 493: 562-70.
  5. Kersten, M. and Smedes, F., 2002. Normalization procedures for sediment contaminants in spatial and temporal trend monitoring. Journal of Environmental Monitoring, 4(1): 109-115.
  6. Keshavarzi, B., Mokhtarzadeh, Z., Moore, F., Rastegari Mehr, M., Lahijanzadeh, A., Rostami, S. and Kaabi, H., 2015. Heavy metals and polycyclic aromatic hydrocarbons in surface sediments of Karoon River, Khuzestan Province, Iran. Environmental Science and Pollution Research volume 22, 19077–19092.
  7. Khan, M.F., Latif, M.T., Lim, C.H., Amil, N., Jaafar, S.A., Dominick, D., Nadzir, M.S.M., Sahani, M. and Tahir, N.M., 2015. Seasonal effect and source apportionment of polycyclic aromatic hydrocarbons in PM2.5. Atmospheric Environment, 106: 178-190.
  8. Lang, Y., Wang, N., Gao, H. and Bai, J., 2012. Distribution and risk assessment of polycyclic aromatic hydro - carbons (PAHs) from Liaohe estuarine wetland soils. Environmental Monitoring and Assessment. 184(9): 5545-52.
  9. Law, R.J., Dawes, V.J., Woodhead, R.J. and Matthiessen, P., 1997. Polycyclic aromatic hydrocarbons (PAH) in seawater around England and Wales. Marine Pollution Bulletin, 34: 306–322.
  10. Liu, Y., Chen, L., Huang, Q., Li, W., Tang, Y. and Zhao, J., 2009. Source apportionment of polycyclic aromatic hydrocarbons (PAHs) in surface sediments of the Huangpu River, Shanghai, China. Science of the Total Environment, 407(8): 2931-2938.
  11. Maskaoui, K., Zhou, J.L., Hong, H.S. and Zhang, Z.L., 2002. Contamination by polycyclic aromatic hydrocarbons in the Jiulong River Estuary and Western Xiamen Sea, China. Environmental Pollution, 118: 109, 122.
  12. Mirza, R., Mohammadi, M., Dadollahi Sohrab, A., Abedi, E. and Fakhri, A., 2011. Polycyclic Aromatic Hydrocarbons (PAHs) in Seawater Intertidal Areas of Boushehr Province (Persian Gulf). Journal of Oceanography. 2 (7):21-29. (in Persian).
  13. Ouyang, Z., Gao, L. and Yang, C., 2018. Distribution, sources and influence factors of polycyclic aromatic hydrocarbon at different depths of the soil and sediments of two typical coal mining subsidence areas in Huainan, China. Ecotoxicology and Environmental Safety, 163: 255-265.
  14. Rahmanpoor, S., Ghafourian, H., Hashtroudi, S.M., Rabani, M., Mehdinia, A. and Darvish Bastami, K., 2012. The Study of Polycyclic Aromatic Hydrocarbons (PAHs) Contamination in Sediments of Hormoz Straight - Persian Gulf. Journal of Oceanography, 3 (10): 37-44. (in Persian).
  15. Simoneit, B.R.T., 2002. Biomass burning – a review of organic tracers for smoke from incomplete combustion. Apply Geochemistry 17: 129–162.
  16. Tam, N.F.Y., Ke, L., Wang, X.H. and Wong, Y.S., 2001. Contamination of polycyclic aromatic hydrocarbons in surface sediments of mangrove swamp. Environmental Pollution. 114, 255-263.
  17. Tobiszewski, M. and Namieśnik, J., 2012. PAH diagnostic ratios for the identification of pollution emission sources. Environmental Pollution, 162: 110-119pp.
  18. Tolosa, I., de Mora, S.J., Fowler, S.W., Villeneuve, J., Bartocci, J. and Cattini, C., 2005. Aliphatic and aromatic hydrocarbons in marine biota and coastal sediments from the Gulf and the Gulf of Oman. Marine Pollution Bulletin, 50: 1619–1633.
  19. Wang, Z. and Chen, J., 2007. Polycyclic aromatic hydrocarbons in Dalian soils: distribution and toxicity assessment. Journal of Environmental Monitoring. 9(2): 199-204.
  20. Winiarczyk, B. and Namyslowski, G., 2007. The concentration of the chosen smoke toxicity biomarkers among smokers suffering from larynx cancer. The Polish Journal of Otolaryngology, 61(1): 39-46.