Utilization of chitosan-coated superparamagnetic iron oxide nanoparticles for chromium removal
- 263 Downloads
Superparamagnetic iron oxide nanoparticles (SPIONs) have been widely used for their versatility, while it is coated with a biopolymer like chitosan that adds attraction and also increases its applications. In this study, SPION was synthesized by chemical co-precipitation method, characterized using various analytical techniques like UV–Vis, FTIR, SEM, EDX, TEM, AFM, XRD, zeta potential and Raman spectroscopy analysis. Chitosan was coated onto the SPIONs and used for water treatment to remove chromium (450 ppm concentration). Chitosan-coated SPIONs were found to remove about 80% of chromium. Freundlich model was found to be fitting better for the current study.
KeywordsChitosan SPIONs Metal removal Characterization Chromium
In today’s world, alarming water pollution has become a major threat to the environment and has led to the development of new technologies to minimize the potential contaminants from the water bodies. Effluents from the mining industries, power generating industries, electronic industries and tanneries contain large amounts of heavy metals that pose a great risk to the surviving population in and around the water bodies (Liu et al. 2012) and cause bioaccumulation in beings that ingest these waters directly or indirectly (Yousafzai et al. 2017). Heavy metals such as uranium, mercury, chromium, arsenic, lanthanum, lead, cadmium and zinc are few of the commonly found metals that contaminate the water bodies (Boddu et al. 2003; Tchounwou et al. 2012). Chromium (Cr, Z = 24, A = 51.9961 u ± 0.0006 u) is said to be relatively stable among the heavy metal ions of the periodic table and exists in several ionic forms. It is toxic and it is considered to be one of the major carcinogens as well as a mutagenic compound (Geng et al. 2009; Dayan and Paine 2001; Aitio et al. 1988). Thus, removal of this hazardous heavy metal has become a major goal and research interest among several researchers and led to the development of diverse methods. Although several methods have been devised, bio-sorption using bio-based particles/nanoparticles has been considered highly efficient (Lasheen et al. 2013; Sheet et al. 2014; Abdel-Raouf and Abdul-Raheim 2017; Mane et al. 2011; Ahluwalia and Goyal 2007) due to the large surface-to-volume ratio of nanoparticles compared to the bulk materials (Rajput et al. 2016). Using SPIONs is the better option, since superparamagnetic iron oxide nanoparticles (SPIONs) obey to external magnetic field; thus, it is easier to remove after the adsorption process (Gill et al. 2017) and also it is low toxic and non-reactive to human and majorly it has very strong adsorption capacity (Lasheen et al. 2013). Further, crystallinity, dispersion, size and shape also play an important role in the removal of heavy metals efficiently. One of the major challenges of aggregation faced by SPIONs can be overcome by surface modification or by following up certain parameters (coating a sorbent material) that result in the formation of monodispersed SPIONs (Justin et al. 2018; Mahmoudi et al. 2011).
In order to increase the chemisorption efficiency of SPIONs, biopolymers such as chitosan can be used to coat the nanoparticles. Chitosan is an abundant biodegradable biopolymer available in the nature, which can be extracted from the exoskeletons of marine organisms such as crabs, lobsters, shrimps as well as fungi. Literature studies have suggested that chitosan is more efficient than its precursor chitin (Boddu et al. 2003). The free amine groups present on the surface of chitosan aid in the chemisorption of the metal ions and subsequently result in their removal from wastewater (Kaveeshwar et al. 2018). The coating of chitosan on SPIONs makes it less toxic to the environment resulting in an eco-friendly method of heavy metal removal. This use of nanoparticles in this method is highly cost-effective process (Gill et al. 2017) and hence can be executed in a large-scale clean-up processes. In this study, SPIONs were synthesized by chemical method, coated with chitosan and utilized for chromium removal from water.
Materials and methods
All chemicals used in this work were of analytical grade. Ferrous sulphate and ferric sulphate were procured from M/s Merck, India. Ammonia solution, tetramethyl ammonium hydroxide solution (TMAOH) and chitosan were obtained from SRL, India; acetic acid was purchased from Fisher Chemical, India. Potassium dichromate was obtained from Rankem, India.
Synthesis of superparamagnetic iron oxide nanoparticles (SPIONs)
SPIONs were synthesized by following chemical co-precipitation method. The synthesis procedure is as follows: 0.91 g ferrous sulphate (FeSO4) and 3.2 g ferric sulphate (Fe2(SO4)3) were taken in 8 ml and 2 ml nitrogenated Milli-Q water, respectively, and stirred well. The two solutions were mixed together while manually stirring it for 15 min. 15 ml of 25% ammonia solution was added dropwise to the precursor solution under constant vigorous stirring, and 15 ml of 25% TMAOH was also added dropwise to the solution. As soon as the colour of the solution turned black, the addition of ammonia and TMAOH was stopped. The nanoparticles were allowed to settle using a magnet, and excess reducing agent was pipetted out. Nanoparticles were washed several times with Milli-Q water until the pH dropped to neutral. Further, the nanoparticles were lyophilized in vacuum to obtain powder particles (Eom et al. 2010).
Preparation of chitosan-coated SPIONs
Chitosan-coated SPIONs were prepared according to the protocol followed by Sureshkumar et al. (2016) with some modifications. 100 mg of chitosan was added to 40% acetic acid and stirred for 24 h. Then, 100 mg of SPIONs was added and was sonicated for 30 min. The sample was then lyophilized in vacuum.
Characterization of SPIONs
The prepared SPIONs were characterized for further studies. Absorbance spectrum of SPIONs was recorded at UV–Vis spectrometer. Fourier transform infrared spectroscopy (FTIR) of prepared SPIONs was analysed using IR Affinity-1s, Shimadzu, Japan, for wave number range of 4000–400 cm−1. Microscopic analysis was investigated using transmission electron microscope (TEM) (TEECNAI G2 Spirit Biotwin—120 kV) and atomic force microscopy (AFM) (Bruker, Germany). X-ray diffraction (XRD) patterns of the SPIONs were recorded by Smartlab X-ray diffractometer (Rigaku, Japan). The XRD patterns were taken in the 2θ range of 20°–80° in a fixed-time mode at room temperature. To determine the stability of the SPIONs, zeta potential value was recorded (Brookhaven ZetaPALS). Raman spectroscopy was also performed using LabRam HR 800 model of Horiba Jobinyvon.
Chromium metal removal
Results and discussion
Characterization of SPIONs and chitosan-coated SPIONs
Chromium metal adsorption studies
Summary and conclusions
The chemical structure and the morphology of SPIONs and chitosan-coated SPIONs had been investigated. SPIONs coated with chitosan were interacting better with chromium and improved the heavy metal adsorption. The major reason must be the interaction between amine of chitosan and heavy metal leading to covalent bonding. Once the bonding is happening between the chitosan-coated SPIONs and heavy metal, removal of these SPIONs out of the water is easier as it can be removed by applying external magnetic field. Thus, it can be employed for efficient removal of chromium ion from wastewater.
Compliance with ethical standards
Conflict of interest
The authors declare no conflict of interest.
- Abdel-Raouf MS, Abdul-Raheim ARM (2017) Removal of heavy metals from industrial waste water by biomass-based materials: a review. J Pollut Eff Control 5:180Google Scholar
- Gill SK, Singh G, Khatri M (2017) Synthesis and characterization of superparamagnetic iron oxide nanoparticles for water purification applications. Int J Eng Technol Sci Res 4(4):355–359Google Scholar
- Lasheen MR, El-Sherifa IY, Sabryb DY, El-Wakeela ST, El-Shahat MF (2013) Removal and recovery of Cr(VI) by magnetite nanoparticles. Desalination Water Treat 52(34–36):1–10Google Scholar
- Mane P, Bhosle AB, Jangam CM, Vishwakarma CV (2011) Bioadsorption of selenium by pretreated algal biomass. Adv Appl Sci Res 2:202Google Scholar
- Sarkar ZK, Sarkar FK (2013) Selective removal of lead (II) ion from wastewater using superparamagnetic monodispersed iron oxide (Fe3O4) nanoparticles as a effective adsorbent. Int J Nanosci Nanotechnol 9(2):109–114Google Scholar
- Tchounwou PB, Yedjou CG, Patlolla AK, Sutton DJ (2012) Heavy metal toxicity and the environment. EXS 101:133–164Google Scholar
- Yousafzai AM, Ullah F, Bari F, Raziq S, Riaz M, Khan K, Nishan U, Sthanadar IA, Shaheen B, Shaheen M, Ahmad H (2017) Bioaccumulation of some heavy metals: analysis and comparison of Cyprinus carpio and Labeo rohita from Sardaryab, Khyber Pakhtunkhwa. BioMed Research International, CairoGoogle Scholar
Open AccessThis article is 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, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.