Effects of chelating ligands on the kinetics of Pb release from montmorillonite as a prevalent clay mineral in arid and semi-arid regions

Document Type : Research Paper

Authors

1 Scientific member of Soil Conservation and Watershed Management, Isfahan Agricultural and Natural Resources Research and Education Center, AREEO, Isfahan, Iran.

2 Associate Professor of Soil Science, Department of Soil Science, College of Agriculture, Isfahan University of Technology, Isfahan, Iran.

3 Professor of Soil Science, Department of Soil Science, College of Agriculture, Isfahan University of Technology, Isfahan, Iran.

10.29252/aridbiom.2021.17112.1869

Abstract

Contamination with heavy metals such as leads resulting from human catastrophic excavation activities is one of the serious soil problems in arid and semi-arid region. So, remediation of these kinds of contaminations is one of priorites to protect the soil of these areas. In soil and sediment environments, the potential bioavailability and mobility of metals are predominantly regulated by adsorption/desorption reactions at the mineral-water interface. Although numerous studies have been devoted to understanding the adsorption of metals onto minerals, less is known about desorption processes, especially their kinetics, under the influence of organic ligands. In this study, desorption of Pb from montmorillonite (MMT) was studied as effected by biodegradable chelating ligands, i.e. methylglycine diacetic acid (MGDA) and glutamic-N,Ndiaceticacid (GLDA), at two concentrations (0.25 and 1.0 mM) were compared with that of ethylenediaminetetraaceticacid (EDTA). The results showed that Pb desorption was rapid, reaching equilibrium in a relatively short time (within 3 h). The degree of Pb desorption was proven to be governed by the presence and concentration of the chelating agents. The capacity of the chalants for removing Pb from MMT was in the order EDTA>MGDA>GLDA. Approximately 12%, 19%, and 23% of the sorbed Pb was desorbed by 0.25 mM of GLDA, MGDA, and EDTA, respectively. The corresponding desorptions in the presence of 1.00 mM of the same ligands were 47%, 59%, and 93%, respectively. Therefore, it can be predicted that the presence of biodegradable ligands, i.e. GLDA and MGDA compared to EDTA will create less mobility of Pb in the environment and consequently we will have less pollution in soil and water environments. Owing to soil alkalinity in arid and semi-arid region, it seems that using biodegradable ligands can desorbtion of lead from soil, minimizing the risk of under water contamination.

Keywords


 [1]. Adrees, M., Ali, S., Rizwan, M., Zia-ur-Rehman, M., Ibrahim, M., Abbas, F., Irshad, M. K. (2015). Mechanisms of silicon-mediated alleviation of heavy metal toxicity in plants: a review. Ecotoxicology and Environmental Safety, 119, 186-197.
]2]. Ahmed, M. J. K., Ahmaruzzaman, M. (2016). A review on potential usage of industrial waste materials for binding heavy metal ions from aqueous solutions. Journal of Water Process Engineering, 10, 39-47.
]3]. Akcil, A., Erust, C., Ozdemiroglu, S., Fonti, V., Beolchini, F. (2015). A review of approaches and techniques used in aquatic contaminated sediments: metal removal and stabilization by chemical and biotechnological processes. Journal of Cleaner Production, 86, 24-36.
]4]. Akpomie, K. G., Dawodu, F. A., Adebowale, K. O. (2015). Mechanism on the sorption of heavy metals from binary-solution by a low cost montmorillonite and it does desorption potential. Alexandria Engineering Journal, 54(3), 757-767.
]5]. BASF. 2007. Technical Information (Ti/EVD 1418 e), Trilon® M types, BASF.
]6]. Begum, Z. A., Rahman, I. M., Tate, Y., Egawa, Y., Maki, T., Hasegawa, H. (2012). Formation and stability of binary complexes of divalent ecotoxic ions (Ni, Cu, Zn, Cd, Pb) with biodegradable aminopolycarboxylate chelants (dl-2-(2-carboxymethyl) nitrilotriacetic acid, GLDA, and 3-hydroxy-2, 2′-iminodisuccinic acid, HIDS) in aqueous solutions. Journal of Solution Chemistry, 41(10), 1713-1728.
]7]. Bilgin, M., Tulun, S. (2016). Removal of heavy metals (Cu, Cd and Zn) from contaminated soils using EDTA and FeCl3. Global Nest Journal, 18, 98-107.
]8]. Bisinger Jr, E. (2009, June). Dissolvine GL: A new, biodegradable chelating agent with an excellent safety profile. In 13th Annual Green Chemistry & Engineering Conference (pp. 23-25). MD, USA: College Park.
]9]. Cao, A., Carucci, A., Lai, T., La Colla, P., Tamburini, E. (2007). Effect of biodegradable chelating agents on heavy metals phytoextraction with Mirabilis Jalapa and on its associated bacteria. European Journal of Soil Biology, 43(4), 200-206.
]10]. Carocci, A., Catalano, A., Lauria, G., Sinicropi, M. S., & Genchi, G. (2016). Lead toxicity, antioxidant defense and environment. Reviews of environmental contamination and toxicology, 45-67.
]11]. Dissolvine, G. L. (2011). Technical Brochure. AkzoNobel Functional Chemicals BV. Amsterdam. Netherlands.
]12]. Dumat, C., Shahid, M., Khalid, S., Murtaza, B. (2020). Lead pollution and human exposure: forewarned is forearmed, and the question now becomes how to respond to the threat! In Lead in Plants and the Environment (pp. 33-65). Springer, Cham.
]13]. Eick, M. J., Peak, J. D., Brady, P. V., Pesek, J. D. (1999). Kinetics of lead adsorption/desorption on goethite: Residence time effect. Soil Science, 164(1), 28-39.
]14]. Garman, S. M., Eick, M. J., Beck, M. (2007). Desorption kinetics of lead from goethite: Effect of residence time and mixing. Soil science, 172(3), 177-188.
]15]. Guo, X., Zhang, G., Wei, Z., Zhang, L., He, Q., Wu, Q., Qian, T. (2018). Mixed chelators of EDTA, GLDA, and citric acid as washing agent effectively remove Cd, Zn, Pb, and Cu from soils. Journal of soils and sediments, 18(3), 835-844.
]16]. Hamidpoor, M. (2009). Sorption and Desorption of Cadmium and Lead on Zeolite and Bentonite. Phd. thesis. Isfahan University of Technology, Isfahan, Iran.150 pp. (in Farsi)    
]17]. Igberase, E., Osifo, P. (2015). Equilibrium, kinetic, thermodynamic and desorption studies of cadmium and lead by polyaniline grafted cross-linked chitosan beads from aqueous solution. Journal of Industrial and Engineering Chemistry, 26, 340-347.
]18]. Inyang, H. I., Onwawoma, A., Bae, S. (2016). The Elovich equation as a predictor of lead and cadmium sorption rates on contaminant barrier minerals. Soil and Tillage Research, 155, 124-132.
]19]. KolodyƄska, D. (2010). The biodegradable complexing agents as an alternative to chelators in sorption of heavy metal ions. Desalination and Water Treatment, 16(1-3), 146-155.
]20]. Li, Y., Wang, J. D., Wang, X. J., Wang, J. F. (2012). Adsorption–desorption of Cd (II) and Pb (II) on Ca-montmorillonite. Industrial & engineering chemistry research, 51(18), 6520-6528.
]21]. Mahar, A., Wang, P., Ali, A., Awasthi, M. K., Lahori, A. H., Wang, Q., Zhang, Z. (2016). Challenges and opportunities in the phytoremediation of heavy metals contaminated soils: a review. Ecotoxicology and environmental safety, 126, 111-121.
]22]. Mermut, A. R., Cano, A. F. (2001). Baseline studies of the clay minerals society source clays: chemical analyses of major elements. Clays and Clay Minerals, 49(5), 381-386.
]23]. Moghal, A. A. B., Mohammed, S. A. S., Almajed, A., Al-Shamrani, M. A. (2020). Desorption of heavy metals from lime-stabilized arid-soils using different extractants. International Journal of Civil Engineering, 18(4), 449-461.
]24]. Nörtemann, B. (2005). Biodegradation of Chelating Agents: EDTA, Dtpa, Pdta, Nta, and Edds.
]25]. Pinto, I. S., Neto, I. F., Soares, H. M. (2014). Biodegradable chelating agents for industrial, domestic, and agricultural applications a review. Environmental Science and Pollution Research, 21(20), 11893-11906.
]26]. Rahman, I. M. M., Hossain, M. M., Begum, Z. A., Rahman, M. A., Hasegawa, H. (2011). Eco-environmental consequences associated with chelant-assisted phytoremediation of metal-contaminated soil. Handbook of phytoremediation, 709-722.
]27]. Saifullah, Ghafoor, A., Zia, M. H., Murtaza, G., Waraich, E. A., Bibi, S., Srivastava, P. (2010). Comparison of organic and inorganic amendments for enhancing soil lead phytoextraction by wheat (Triticum aestivum L.). International journal of phytoremediation, 12(7), 633-649.
]28]. Shahid, M., Austruy, A., Echevarria, G., Arshad, M., Sanaullah, M., Aslam, M., Dumat, C. (2014). EDTA-enhanced phytoremediation of heavy metals: a review. Soil and Sediment Contamination: An International Journal, 23(4), 389-416.
]29]. Shirvani, M., Shariatmadari, H., Kalbasi, M. (2007). Kinetics of cadmium desorption from fibrous silicate clay minerals: Influence of organic ligands and aging. Applied Clay Science, 37(1-2), 175-184.
]30]. Srivastava, P., Gräfe, M., Singh, B., Balasubramanian, M. (2007). Cadmium and lead desorption from kaolinite. Developments in Earth and Environmental Sciences, 7, 205-233.
]31]. Uddin, M. K. (2017). A review on the adsorption of heavy metals by clay minerals, with special focus on the past decade. Chemical Engineering Journal, 308, 438-462.
]32]. Wang, G., Zhang, S., Xu, X., Zhong, Q., Zhang, C., Jia, Y., Li, Y. (2016). Heavy metal removal by GLDA washing: optimization, redistribution, recycling, and changes in soil fertility. Science of the Total Environment, 569, 557-568.
]33]. Wang, X. S., Liu, F., Lu, H. J., Zhang, P., & Zhou, H. Y. (2011). Adsorption kinetics of Cd (II) from aqueous solution by magnetite. Desalination and Water Treatment, 36(1-3), 203-209.
]34]. Yu, M. H., Tsunoda, H. (2004). Environmental toxicology: biological and health effects of pollutants.  CRC press.