Comparative Study of the Adsorption and Desorption Behavior of Single and Multi-Ring Aromatics in Sediment Fractions

Abstract

The sorption behaviour of benzene, toluene, ethyl benzene, xylene and naphthalene using clay and sand sediments under ambient conditions is examined in this study. Experimental results showed that, the time taken to attain adsorption equilibrium for naphthalene, and BTEX were 28, 30, 30, 32, 28 hrs and 20, 22, 22, 24, 22 hrs while the desorption equilibrium time were 10, 13, 12, 15, 12 hrs and 9, 9, 9, 11, 10 hrs in clay and sand respectively. All of the naphthalene, and BTEX were adsorbed at the different equilibrium times, using clay while the amount of naphthalene and BTEX adsorbed by sand, at different equilibrium times were 117, 121, 127, 123 and 134 mg. Following the results of the adsorption/desorption experiments, quantitative measurements showed that sand exhibited higher affinity for the solute as retained more chemicals (as high as between 58% - 66%) within it pores while nearly all the chemicals adsorbed by the clay were released at the attainment of equilibrium. The implication of this is that occlusion within the sand particles may likely be the resultant effect of continued sand-chemicals contact. The amount of contaminant solute adsorbed and desorbed affirmed that clay has a better capacity to retain naphthalene and BTEX than sand and this may not be unrelated to its large surface area, high porosity and higher hydraulic conductivity for the solutes arising from its good binding sites (small pore sizes) that tend to hold the adsorbates to its particles.

Share and Cite:

C. Owabor, S. Agarry, B. Ayodele, I. Udeh and E. Ehiosun, "Comparative Study of the Adsorption and Desorption Behavior of Single and Multi-Ring Aromatics in Sediment Fractions," Advances in Chemical Engineering and Science, Vol. 3 No. 1, 2013, pp. 67-73. doi: 10.4236/aces.2013.31007.

Conflicts of Interest

The authors declare no conflicts of interest.

References

[1] D. T. Sponza and R. Oztekin, “Destruction of Some More and Less Hydrophobic PAHs and Their Toxicities in a Petrochemical Industry Wastewater with Sonication in Turkey,” Bioresource Technology, Vol. 101, No. 22, 2010, pp. 8639-8648. doi:10.1016/j.biortech.2010.06.124
[2] J. D. Stokes, G. I. Paton and K. T. Semple, “Behavior and Assessment of Bioavailability of Organic Contaminants in Soil: Relevance for Risk Assessment and Remediation,” Soil Use and Management, Vol. 21, No. S2, 2006, pp. 475-486. doi:10.1079/SUM2005347
[3] W. Chen, L. Cong, H. Hu, P. Zhang, J. Li, Z. Feng, A. T. Kan and M. B. Tomson, “Release of Adsorbed Polycyclic Aromatic Hydrocarbons under Cosolvent Treatment: Implications for Availability and Fate,” Environmental Toxicology and Chemistry, Vol. 27, No. 1, 2008, pp. 112-118. doi:10.1897/07-170.1
[4] J. Yan, L. Wang, P. P. Fu and H. Yu, “Photomutagenicity of 16 Polycyclic Aromatic Hydrocarbons from the US EPA Priority Pollutant List,” Mutation Research/Genetic Toxicology and Environmental Mutagenesis, Vol. 557, No. 1, 2004, pp. 99-108. doi:10.1016/j.mrgentox.2003.10.004
[5] H. K. Bojes and P. G. Pope, “Characterization of EPA’s 16 Priority Pollutant Polycyclic Aromatic Hydrocarbons (PAHs) in Tank Bottom Solids and Associated Contaminated Soils at Oil Exploration and Production Sites in Texas,” Regulatory Toxicities and Pharmacology, Vol. 47, No. 3, 2007, pp. 288-295. doi:10.1016/j.yrtph.2006.11.007
[6] M. C. Bruzzoniti, M. Fungi and C. Sarzanini, “Determination of EPA’s Priority Pollutant Polycyclic Aromatic Hydrocarbons in Drinking Waters by Solid Phase Extraction-HPLC,” Analytical Methods, Vol. 21, No. 6, 2010, pp. 739-743. doi:10.1039/b9ay00203k
[7] S. Mitra and R. Pranab, “BTEX: A Serious Ground Water Contaminant,” Research Journal of Environmental Sciences, Vol. 5, 2011, pp. 394-398. doi:10.3923/rjes.2011.394.398
[8] E. F. Neuhauser, J. P. Kreitinger, D. V. Nakles, S. B. Hawthorne, F. G. Doherty, U. Ghosh, M. F. Khalil, R. S. Ghosh, M. T. O. Jonker and S. A. Van der Heijden, “Bio-availability and Toxicity of PAHs at MGP Sites,” Land Contamination and Reclamation, Vol. 14, No. 2, pp. 261-266. doi:10.2462/09670513.713
[9] C. N. Owabor, S. E. Agarry and T. O. Azeez, “Development of a Transport Model for the Microbial Degradation of Polycyclic Aromatic Hydrocarbons in a Saturated Porous Medium,” Journal of the Nigerian Association of Mathematical Physics, Vol. 16, No. 2, 2010, pp. 317-324.
[10] W. Zhang, E. J. Bouwer and W. P. Ball, “Bioavailability of Hydrophobic Organic Contaminants: Effects and Implications of Sorption-Related Mass Transfer on Bioremediation,” Ground Water Monitoring & Remediation, Vol. 18, No. 1, 1998, pp. 126-138.
[11] C. N. Owabor, S. E. Ogbeide and A. A. Susu, “Adsorption and Desorption Kinetics of Naphthalene, Anthracene and Pyrene in Soil Matrix,” Petroleum Science and Technology, Vol. 28, No. 5, 2010, pp. 504-514. doi:10.1080/10916460802108546
[12] C. N. Owabor, S. E. Ogbeide and A. A. Susu, “Estimation of Transport and Degradation Parameters for Naphthalene and Anthracene: Influence of Mass Transfer on Kinetics,” Environmental Monitoring and Assessment, Vol. 169, No. 1-4, 2010, pp. 607-617. doi:10.1007/s10661-009-1200-6
[13] S. Y. Gebremariam, “Mineralization, Sorption and Desorption of Chlorpyrifos in Aquatic Sediments and Soils,” Ph.D. Thesis, Washington State University, Pullman, 2011.
[14] C. F. Chang, C. Y. Chang, K. H. Chen, W. T. Tsai, J. L. Shie and Y. H. Chen, “Adsorption of Naphthalene on Zeolite from Aqueous Solution,” Journal of Colloid and Interface Science, Vol. 277, No. 1, 2004, pp. 29-34. doi:10.1016/j.jcis.2004.04.022
[15] Z. Yu, W. Huang, J. Song, Y. Qian and P. Peng, “Sorption of Organic Pollutants by Marine Sediments: Implication for the Role of Particulate Organic Matter,” Chemosphere, Vol. 65, No. 11, 2006, pp. 2493-2501. doi:10.1016/j.chemosphere.2006.04.036
[16] R. S. Kookana, “The Role of Biochar in Modifying the Environmental Fate, Bioavailability and Efficacy of Pesticides in Soils: A Review,” Soil Research, Vol. 48, No. 7, 2010, pp. 627-637. doi:10.1071/SR10007
[17] C. N. Owabor and J. O. Osarumwense, “Pyrene Mineralization in Clay Soil with and without Organic Carbon: The Role of Adsorption and Desorption Kinetics Equilibria,” Global Journal of Pure and Applied Sciences, Vol. 14, No. 1, 2008, pp. 109-113. doi:10.4314/gjpas.v14i1.16782
[18] H. M. Lesan and A. Bhandari, “Atrazine Sorption on Surface Soils: Time-Dependent Phase Distribution and Apparent Desorption Hysteresis,” Water Research, Vol. 37, No. 7, 2003, pp. 1644-1654. doi:10.1016/S0043-1354(02)00497-9
[19] P. Wang and A. A. Keller, “Sorption and Desorption of Atrazine and Diuron onto Water Dispersible Soil Primary Size Fractions,” Water Research, Vol. 43, No. 5, 2009, pp. 1448-1456. doi:10.1016/j.watres.2008.12.031
[20] W. J. Weber Jr. and J. C. Morris, “Kinetics of Adsorption on Carbon from Solution,” Journal of the Sanitary Engineering Division, Vol. 89, No. 2, 1963, pp. 31-59.
[21] J. J. Pignatello and B. Xing, “Mechanisms of Slow Sorption of Organic Chemicals to Natural Particles,” Environmental Science & Technology, Vol. 30, No. 1, 1996, pp. 1-11. doi:10.1021/es940683g
[22] W. Huang, “Effects of Organic Matter Heterogeneity on Sorption and Desorption of Organic Contaminants by Soils and Sediments,” Applied Geochemistry, Vol. 18, No. 7, 2003, pp. 955-972.
[23] W. L. McCabe, J. C. Smith and P. Harriot, “Unit Operations of Chemical Engineering,” 7th Edition, McGraw-Hill, New York, 2005, pp. 836-888.
[24] C. N. Owabor and S. E. Agarry, “Sorption Behaviour of Naphthalene in Clay and cCoarse Sediments Kinetic and Equilibrium Studies,” Nigerian Journal of Applied Science, Vol. 27, 2009, pp. 15-23.
[25] R. Sivaraj, C. Namasivayan and K. Kadirvelu, “Orange Peel as an Adsorbent in the Removal of Acid Violet 17 (Acid Dye) from Aqueous Solution,” Water Management, Vol. 21, No. 1, 2001, pp. 105-110.
[26] M. N. Sahmoune, K. Louhab and A. Boukhiar, “Kinetic and Equilibrium Models for the Biosorption of Cr(III) on Streptomyces rimosus,” Journal of Applied Sciences Research, Vol. 3, No. 4, 2008, pp. 294-301.
[27] W. J. Weber and T. M. Young, “A Distribute Reactivity Model for Sorption by Soils and Sediments. 6. Mechanistic Implications of Desorption under Supercritical Fluid Conditions,” Environmental Science and Technology, Vol. 31, No. 6, 1997, pp. 1686-1691. doi:10.1021/es9605681
[28] S. Singh, L. K. Verma, S. S. Sambi and S. K. Sharma, “Adsorption Behavior of Ni(II) from Water onto Zeolite X: Kinetics and Equilibrium Studies,” Proceedings of the World Congress on Engineering and Computer Science, 22-24 Octber 2008, San Francisco, pp. 112-117.
[29] C. W. Curry, R. H. Bennett, M. H. Hulbert, K. J. Curry and R. W. Faas, “Comparative Study of Sand Porosity and a Technique for Determining Porosity of Undisturbed Marine Sediment,” Marine Georesource and Geotechnology, Vol. 22, No. 4, 2004, pp. 231-252. doi:10.1080/10641190490900844
[30] C. N. Owabor, I. O. Oboh and F. A. Omiojieahior, “Adsorption Isotherms for Naphthalene on Clay and Silt Soil Fractions: A Comparison of Linear and Nonlinear Methods,” Advanced Materials Research, Vol. 367, 2012, pp. 359-364. doi:10.4028/www.scientific.net/AMR.367.359
[31] U. V. Okere and K. T. Semple, “Biodegradation of PAHs in ‘Pristine’ Soils from Different Climate Region,” Journal of Bioremediation & Biodegradation, Vol. 3, 2012, p. 145.

Copyright © 2024 by authors and Scientific Research Publishing Inc.

Creative Commons License

This work and the related PDF file are licensed under a Creative Commons Attribution 4.0 International License.