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Determination of Sulphur Dioxide Air Emission of Refined Petroleum Products by Emission Factor Approach for Air Pollution Control

Received: 22 March 2024    Accepted: 7 April 2024    Published: 28 April 2024
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Abstract

Air pollution control is a safe method for achieving a sustainable environment and can be accomplished by adequately monitoring pollutants that pose significant environmental risks. The combustion of sulfur-containing petroleum products has been a major concern for several decades. Therefore, this study was aimed at determining sulfur levels in refined petroleum products such as Premium Motor Spirit (PMS), Automotive Gas Oil (AGO), and Dual-Purpose Kerosene (DPK). It also investigated the air quality implications of sulfur levels and estimated the contribution of the refinery’s products to sulfur dioxide air emission. Fuel samples were collected from the Warri Refining and Petrochemical Company (WRPC) in Nigeria and analyzed using Ultraviolet-visible spectrophotometer (UV-Vis) and Energy-Dispersive X-ray Fluorescence (EDXRF). Sulfur levels were determined at 425 nm wavelength, and sulfur dioxide air emission were estimated for seven consecutive years from 2010 to 2016 using the emission factor approach. The densities of PMS, AGO, and DPK were 0.77 kg/l, 0.832 kg/l, and 0.82 kg/l respectively. The levels of sulfur in PMS, AGO, and DPK were 2.007 x 10-4 %, 6.970 x 10-5 wt%, and 4.233 x 10-5 wt% respectively from UV-Vis technique and 0.016, 0.087 and 0.029% respectively for EDXRF technique were found below the sulfur limit of 0.015 %, 0.005 % and 0.015 % for PMS, AGO and DPK respectively specified by Standard Organization of Nigeria (SON) specifications of 0.1, 0.5 and 0.15wt% for PMS, AGO and DPK respectively. The annual sulfur dioxide emissions were obtained for seven consecutive years from 2010 to 2016. The results from UV-VIS were observed to have the highest SO2 emission of 0.1718 tons for PMS in 2011, 0.2593 tons in 2010 for AGO, and 0.0974 tons for DPK in 2010, while the lowest emission was observed to be 0.029 tons for PMS in 2015, 0.0362 tons in 2015 for AGO and 0.0181 tons for DPK also in 2015. The results from EDXRF technique were observed to have the highest SO2 emission of 13.6939 tons for PMS in 2012, 323.6881 tons for AGO in 2010, and 66.7147 tons for DPK also in 2010, while the lowest emissions for PMS, AGO and DPK were all observed in 2015 to be 2.3122, 45.1872, and 12.4182 tons respectively. The study concluded that the refinery complied with the set requirements.

Published in Journal of Energy, Environmental & Chemical Engineering (Volume 9, Issue 2)
DOI 10.11648/j.jeece.20240902.11
Page(s) 46-55
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Sulfur dioxide, Air pollution, Gasoline, Diesel, Kerosene, UV-VIS Spectrophotometer, Energy Dispersive X-Ray Fluorescence, Emission Factor

References
[1] S. Motesaddi, Y. Hashempour, and P. Nowrouz, “Characterizing of Air Pollution in Tehran: Comparison of Two Air Quality Indices,” cej, vol. 3, no. 9, pp. 749–758, Oct. 2017,
[2] E. Von Schneidemesser, K. Steinmar, E. C. Weatherhead, B. Bonn, H. Gerwig, and J. Quedenau, “Air pollution at human scales in an urban environment: Impact of local environment and vehicles on particle number concentrations,” Science of The Total Environment, vol. 688, pp. 691–700, Oct. 2019,
[3] B. S. Fakinle, E. L. Odekanle, A. P. Olalekan, H. E. Ije, D. O. Oke, and J. A. Sonibare, “Air pollutant emissions by anthropogenic combustion processes in Lagos, Nigeria,” Cogent Engineering, vol. 7, no. 1, p. 1808285, Jan. 2020,
[4] G. Richard, S. Izah, and M. Ibrahim, “Air pollution in the Niger Delta region of Nigeria: Sources, health effects, and strategies for mitigation,” Journal of Environmental Studies, vol. 29, no. 1, pp. 1–15, Mar. 2023.
[5] N. Zen, H. S. Huboyo, M. S. Romadhon, J. A. Fatkhurrahman, and S. K. Amrulah, “A Low-Cost Instrument to Monitor Sulphur Dioxide Emissions Based on The DOAS Method,” vol. 14, no. 1, 2023.
[6] T. A. Saleh, “Characterization, determination and elimination technologies for sulfur from petroleum: Toward cleaner fuel and a safe environment,” Trends in Environmental Analytical Chemistry, vol. 25, p. e00080, Mar. 2020,
[7] P. Bani et al., “Modest volcanic SO2 emissions from the Indonesian archipelago,” Nat Commun, vol. 13, no. 1, p. 3366, Jun. 2022,
[8] F. B. Sunday, “Total Suspended Solids and Volatile Organic Compounds In The Airshed of A Reconstructed Road Along Lagos-Ibadan Express Way”.
[9] F. Zhang et al., “Sulfur dioxide may predominate in the adverse effects of ambient air pollutants on semen quality among the general population in Hefei, China,” Science of The Total Environment, vol. 867, p. 161472, Apr. 2023,
[10] C. Guo et al., “Long-Term Exposure to Ambient Fine Particulate Matter (PM2.5) and Lung Function in Children, Adolescents, and Young Adults: A Longitudinal Cohort Study,” Environ Health Perspect, vol. 127, no. 12, p. 127008, Dec. 2019,
[11] Y. Liu et al., “Inverse Association between Ambient Sulfur Dioxide Exposure and Semen Quality in Wuhan, China,” Environ. Sci. Technol., vol. 51, no. 21, pp. 12806–12814, Nov. 2017,
[12] H. Héritier et al., “A systematic analysis of mutual effects of transportation noise and air pollution exposure on myocardial infarction mortality: a nationwide cohort study in Switzerland,” European Heart Journal, vol. 40, no. 7, pp. 598–603, Feb. 2019,
[13] N. Wang et al., “Short-term association between ambient air pollution and lung cancer mortality,” Environmental Research, vol. 179, p. 108748, Dec. 2019,
[14] B. S. Fakinle, O. D. Oke, O. A. Odunlami, J. A. Sonibare, F. A. Akeredolu, and O. S. Oni, “Emission characterization and performance of conventional liquefied petroleum gas cookstove burners,” Cogent Engineering, vol. 6, no. 1, p. 1652228, Jan. 2019,
[15] M. A. Fayad, M. T. Chaichan, H. A. Dhahad, and A. A. Al-Amiery, “Reducing the Effect of High Sulfur Content in Diesel Fuel on NOx Emissions and PM Characteristics Using a PPCI Mode Engine and Gasoline–Diesel Blends,” ACS Omega, 2022.
[16] Chuka Anthony Arinze, Olakunle Abayomi Ajala, Chinwe Chinazo Okoye, Onyeka Chrisanctus Ofodile, and Andrew Ifesinachi Daraojimba, “Evaluating The Integration Of Advanced It Solutions For Emission Reduction In The Oil And Gas Sector,” Eng. sci. technol. j., vol. 5, no. 3, pp. 639–652, Mar. 2024,
[17] K. Ekoue-Kovi, S. Murugesan, O. Ugono, S. Pinappu, and J. Weers, “Novel Environmentally Responsible Solvents for Sulfur Removal in Oil and Gas Applications,” in Day 2 Thu, June 29, 2023, The Woodlands, Texas, USA: SPE, Jun. 2023, p. D021S010R003.
[18] S. C. Bajia, R. J. Singh, B. Bajia, and S. Kumar, “Determination of sulfur content in petroleum products – an overview,” Journal of Sulfur Chemistry, vol. 38, no. 4, pp. 450–464, Jul. 2017.
[19] A. Haruna, Z. M. A. Merican, and S. G. Musa, “Recent advances in catalytic oxidative desulfurization of fuel oil – A review,” Journal of Industrial and Engineering Chemistry, vol. 112, pp. 20–36, Aug. 2022.
[20] S. Chavan, H. Kini, and R. Ghosal, “Process for Sulfur Reduction from High Viscosity Petroleum Oils,” IJESD, pp. 228–231, 2012.
[21] S. Houda, C. Lancelot, P. Blanchard, L. Poinel, and C. Lamonier, “Oxidative Desulfurization of Heavy Oils with High Sulfur Content: A Review,” 2018.
[22] R. Y. Mamuad and A. E. S. Choi, “Biodesulfurization Processes for the Removal of Sulfur from Diesel Oil: A Perspective Report,” Energies, vol. 16, no. 6, p. 2738, Mar. 2023,
[23] X. Meng, M. Zhang, and Y. Zhao, “Environmental regulation and green transition: Quasi-natural experiment from China’s efforts in sulfur dioxide emissions control,” Journal of Cleaner Production, vol. 434, p. 139741, Jan. 2024,
[24] S. Niu, Y. Chen, R. Zhang, and Y. Feng, “How does the air pollution control prevention and control action plan affect sulfur dioxide intensity in China”.
[25] R. Javadli and A. De Klerk, “Desulfurization of heavy oil,” Appl Petrochem Res, vol. 1, no. 1–4, pp. 3–19, Mar. 2012.
[26] S. Chen et al., “Efficient biodesulfurization of diesel oil by Gordonia sp. SC-10 with highly hydrophobic cell surfaces,” Biochemical Engineering Journal, vol. 174, p. 108094, Oct. 2021.
[27] “United States Environmental Protection Agency.” [Online]. Available:
[28] “Emission Factor of Sulfur dioxide emission in Uncontrolled PMS, AGO and DPK.” [Online]. Available: Background Document for AP-42 Section 3.3, Gasoline and Diesel Industrial Engines.
[29] “Standard Organization of Nigeria, SON requirements for refined petroleum products.” [Online]. Available:
[30] O. S. Olatunji, L. A. Jimoda, B. S. Fakinle, J. A. Adeniran, and J. A. Sonibare, “Total Sulfur Levels in Refined Petroleum Products of Southwestern Nigeria Using UV/VIS Spectrophotometer,” Petroleum Science and Technology, vol. 33, no. 1, pp. 102–109, Jan. 2015,
[31] R. Wang, G. Zhang, and H. Zhao, “Polyoxometalate as effective catalyst for the deep desulfurization of diesel oil,” Catalysis Today, vol. 149, no. 1–2, pp. 117–121, Jan. 2010,
[32] Department of Petroleum Resources Annual Oil and Gas Report
[33] R. Wang, F. Yu, G. Zhang, and H. Zhao, “Performance evaluation of the carbon nanotubes supported Cs2.5H0.5PW12O40 as efficient and recoverable catalyst for the oxidative removal of dibenzothiophene,” Catalysis Today, vol. 150, no. 1–2, pp. 37–41, Feb. 2010.
[34] A. O. Ogunkeyede, C. O. Mbaoma, A. D. Iyogbon, A. A. Adebayo, and E. J. Isukuru, “Air Pollution Prediction in Warri and Its Environs Using Quality Parameters,” IJG, vol. 14, no. 06, pp. 531–546, 2023
[35] V. S. Balogun and P. A. O. Odjugo, “Spatial Analyses of Air Pollutants Concentration around the Warri Refining and Petrochemical Company (WRPC), Delta State, Nigeria,” Ghana J. Geography, vol. 14, no. 2, pp. 50–81, Aug. 2022
[36] “Population distribution in Nigeria.” [Online]. Available:
[37] N. Tijjani, P. O. Ike, B. B. Usman, D. I. Malami, and A. Matholo, “Trace Elemental Analysis of Nigerian Petroleum Products Using AAS Method,” ISS N, vol. 3, no. 2, 2012.
[38] “Heating Values of Refined Petroleum Products.” [Online]. Available:
[39] S. M. Farroha, A. E. Habboush, and M. N. Micheal, “Determination of milligram amounts of sulfur in hydrocarbons by constant current coulometry,” Anal. Chem., vol. 56, no. 7, pp. 1182–1183, Jun. 1984,
[40] G. Igile, F. Uboh, U. Luke, S. Ufot, A. Robert, and P. Ebong,“Environmental Quality in Communities around Warri Refining and Petrochemical Company (WRPC), Niger Delta Region, Nigeria,” JSRR, vol. 7, no. 6, pp. 400–412, Jan. 2015.
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    Oni, O., Sonibare, J., Fakinle, B., Oke, D., Odofin, O., et al. (2024). Determination of Sulphur Dioxide Air Emission of Refined Petroleum Products by Emission Factor Approach for Air Pollution Control. Journal of Energy, Environmental & Chemical Engineering, 9(2), 46-55. https://doi.org/10.11648/j.jeece.20240902.11

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    Oni, O.; Sonibare, J.; Fakinle, B.; Oke, D.; Odofin, O., et al. Determination of Sulphur Dioxide Air Emission of Refined Petroleum Products by Emission Factor Approach for Air Pollution Control. J. Energy Environ. Chem. Eng. 2024, 9(2), 46-55. doi: 10.11648/j.jeece.20240902.11

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    AMA Style

    Oni O, Sonibare J, Fakinle B, Oke D, Odofin O, et al. Determination of Sulphur Dioxide Air Emission of Refined Petroleum Products by Emission Factor Approach for Air Pollution Control. J Energy Environ Chem Eng. 2024;9(2):46-55. doi: 10.11648/j.jeece.20240902.11

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  • @article{10.11648/j.jeece.20240902.11,
      author = {Olufemi Oni and Jacob Sonibare and Bamidele Fakinle and Daniel Oke and Odunola Odofin and Motunrayo Oladele and Michael Ikeh},
      title = {Determination of Sulphur Dioxide Air Emission of Refined Petroleum Products by Emission Factor Approach for Air Pollution Control},
      journal = {Journal of Energy, Environmental & Chemical Engineering},
      volume = {9},
      number = {2},
      pages = {46-55},
      doi = {10.11648/j.jeece.20240902.11},
      url = {https://doi.org/10.11648/j.jeece.20240902.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.jeece.20240902.11},
      abstract = {Air pollution control is a safe method for achieving a sustainable environment and can be accomplished by adequately monitoring pollutants that pose significant environmental risks. The combustion of sulfur-containing petroleum products has been a major concern for several decades. Therefore, this study was aimed at determining sulfur levels in refined petroleum products such as Premium Motor Spirit (PMS), Automotive Gas Oil (AGO), and Dual-Purpose Kerosene (DPK). It also investigated the air quality implications of sulfur levels and estimated the contribution of the refinery’s products to sulfur dioxide air emission. Fuel samples were collected from the Warri Refining and Petrochemical Company (WRPC) in Nigeria and analyzed using Ultraviolet-visible spectrophotometer (UV-Vis) and Energy-Dispersive X-ray Fluorescence (EDXRF). Sulfur levels were determined at 425 nm wavelength, and sulfur dioxide air emission were estimated for seven consecutive years from 2010 to 2016 using the emission factor approach. The densities of PMS, AGO, and DPK were 0.77 kg/l, 0.832 kg/l, and 0.82 kg/l respectively. The levels of sulfur in PMS, AGO, and DPK were 2.007 x 10-4 %, 6.970 x 10-5 wt%, and 4.233 x 10-5 wt% respectively from UV-Vis technique and 0.016, 0.087 and 0.029% respectively for EDXRF technique were found below the sulfur limit of 0.015 %, 0.005 % and 0.015 % for PMS, AGO and DPK respectively specified by Standard Organization of Nigeria (SON) specifications of 0.1, 0.5 and 0.15wt% for PMS, AGO and DPK respectively. The annual sulfur dioxide emissions were obtained for seven consecutive years from 2010 to 2016. The results from UV-VIS were observed to have the highest SO2 emission of 0.1718 tons for PMS in 2011, 0.2593 tons in 2010 for AGO, and 0.0974 tons for DPK in 2010, while the lowest emission was observed to be 0.029 tons for PMS in 2015, 0.0362 tons in 2015 for AGO and 0.0181 tons for DPK also in 2015. The results from EDXRF technique were observed to have the highest SO2 emission of 13.6939 tons for PMS in 2012, 323.6881 tons for AGO in 2010, and 66.7147 tons for DPK also in 2010, while the lowest emissions for PMS, AGO and DPK were all observed in 2015 to be 2.3122, 45.1872, and 12.4182 tons respectively. The study concluded that the refinery complied with the set requirements.
    },
     year = {2024}
    }
    

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  • TY  - JOUR
    T1  - Determination of Sulphur Dioxide Air Emission of Refined Petroleum Products by Emission Factor Approach for Air Pollution Control
    AU  - Olufemi Oni
    AU  - Jacob Sonibare
    AU  - Bamidele Fakinle
    AU  - Daniel Oke
    AU  - Odunola Odofin
    AU  - Motunrayo Oladele
    AU  - Michael Ikeh
    Y1  - 2024/04/28
    PY  - 2024
    N1  - https://doi.org/10.11648/j.jeece.20240902.11
    DO  - 10.11648/j.jeece.20240902.11
    T2  - Journal of Energy, Environmental & Chemical Engineering
    JF  - Journal of Energy, Environmental & Chemical Engineering
    JO  - Journal of Energy, Environmental & Chemical Engineering
    SP  - 46
    EP  - 55
    PB  - Science Publishing Group
    SN  - 2637-434X
    UR  - https://doi.org/10.11648/j.jeece.20240902.11
    AB  - Air pollution control is a safe method for achieving a sustainable environment and can be accomplished by adequately monitoring pollutants that pose significant environmental risks. The combustion of sulfur-containing petroleum products has been a major concern for several decades. Therefore, this study was aimed at determining sulfur levels in refined petroleum products such as Premium Motor Spirit (PMS), Automotive Gas Oil (AGO), and Dual-Purpose Kerosene (DPK). It also investigated the air quality implications of sulfur levels and estimated the contribution of the refinery’s products to sulfur dioxide air emission. Fuel samples were collected from the Warri Refining and Petrochemical Company (WRPC) in Nigeria and analyzed using Ultraviolet-visible spectrophotometer (UV-Vis) and Energy-Dispersive X-ray Fluorescence (EDXRF). Sulfur levels were determined at 425 nm wavelength, and sulfur dioxide air emission were estimated for seven consecutive years from 2010 to 2016 using the emission factor approach. The densities of PMS, AGO, and DPK were 0.77 kg/l, 0.832 kg/l, and 0.82 kg/l respectively. The levels of sulfur in PMS, AGO, and DPK were 2.007 x 10-4 %, 6.970 x 10-5 wt%, and 4.233 x 10-5 wt% respectively from UV-Vis technique and 0.016, 0.087 and 0.029% respectively for EDXRF technique were found below the sulfur limit of 0.015 %, 0.005 % and 0.015 % for PMS, AGO and DPK respectively specified by Standard Organization of Nigeria (SON) specifications of 0.1, 0.5 and 0.15wt% for PMS, AGO and DPK respectively. The annual sulfur dioxide emissions were obtained for seven consecutive years from 2010 to 2016. The results from UV-VIS were observed to have the highest SO2 emission of 0.1718 tons for PMS in 2011, 0.2593 tons in 2010 for AGO, and 0.0974 tons for DPK in 2010, while the lowest emission was observed to be 0.029 tons for PMS in 2015, 0.0362 tons in 2015 for AGO and 0.0181 tons for DPK also in 2015. The results from EDXRF technique were observed to have the highest SO2 emission of 13.6939 tons for PMS in 2012, 323.6881 tons for AGO in 2010, and 66.7147 tons for DPK also in 2010, while the lowest emissions for PMS, AGO and DPK were all observed in 2015 to be 2.3122, 45.1872, and 12.4182 tons respectively. The study concluded that the refinery complied with the set requirements.
    
    VL  - 9
    IS  - 2
    ER  - 

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