Page 85 - EER-1-1
P. 85

Explora: Environment
            and Resource                                        Experimental application of GQDs for nuclear materials removal



            1.3. GQDs as smart nanomaterials                   2. Materials and methods

            Recently, some studies have demonstrated that carbon dots   2.1. Reagents
            have various applications, including the ability to be used
            in the manufacture of smart packaging, as they possess   All reagents and solvents used were purchased from
            antimicrobial, antioxidant, flexible, resistant, and moisture-  Sigma-Aldrich, United States, while the radioactive
            impervious properties. 18-20  Similarly, GQDs have also been   material was donated by the Nuclear Energy Research
            applied in several areas, mainly as nanomaterials in the   Institute, Brazil.
            removal of radioactive substances after the detonation of   2.2. Development of GQDs
            a dirty bomb, presenting a viable approach to mitigate and
            reduce the consequences. 21-22                     The method employed for synthesizing GQD dispersions
                                                               was adapted from a previously documented study.  In
                                                                                                          29
              A study carried out by our research group        summary,  this  process involved using  a  graphite  rod  as
            demonstrated that it is feasible to use the surface area of   the anode and a platinum wire as the cathode. For  the
            GQDs to absorb uranium-238 in Alamine 336 solution.   electrolyte, a mixture of 63.5 mL of 0.2 M citric acid and
            In fact, its results corroborated that GQDs can be used as   36.5 mL of 0.2 M sodium citrate was prepared, resulting
            smart devices to reduce the volume of radioactive waste,   in 100  mL of electrolyte solution. The electrochemical
            assisting the entire cycle of the radioactive industry (and   oxidation was carried out for 24 h at a steady current of
            its various interfaces) in dealing with the critical issue of   190 mA, utilizing an ICEL PS-1500 (Icel Manaus, Brazil)
            the final disposal of radioactive waste. 23,24  Furthermore, it
            demonstrates the use of graphene in the adsorptive removal   adjustable power supply. After electrolysis, the resultant
            of uranium ions from wastewater. Graphene was able to   dispersion was filtered to eliminate larger particles. This
            attract heavy and toxic metal ions, including radioactive   filtered mixture was then concentrated by drying at 60°C
            elements, such as uranium, due to its large surface area,   until the volume was reduced to 10  mL. Subsequently,
            electronic properties, tunable surface characteristics, and   50 mL of ethanol was added, and the upper phase, which
            resistance. 25                                     contained the purified GQDs, was separated. These
                                                               purified GQDs were further dried at 60°C until they were
              Due to the properties of GQDs, which include     ready for use.
            chemical  stability, high surface  area, and quantum
            confinement  effects,  their  unique  electronic  properties,   2.3. Characterizations
            coupled with the ability to functionalize their surface   2.3.1. Dynamic light scattering (DLS) for size analysis
            with various groups, make them suitable for interaction
            with a wide range of substances, including radioactive   The size distribution, average size, and polydispersity index
            materials. The potential mechanism by which GQDs   (PDI) of GQDs were analyzed using DLS with a Zetasizer
            can remove radioactive materials involves adsorption.   Nano ZS (Malvern Instruments, United  Kingdom). This
            The high surface area of GQDs provides an extensive   assessment was conducted in triplicate at 25°C using a
            platform for the adsorption of radioactive isotopes.   quartz cuvette of 12 mm² and a laser incidence angle
            Functionalization of GQDs can be tailored to enhance   of 173° relative to the sample. Results were reported as
            their affinity for specific radioactive isotopes, thereby   mean  ±  standard deviation. To address challenges in
            increasing the efficiency of adsorption. In addition, GQDs   analyzing GQDs with DLS, a highly diluted solution
            offer a more targeted approach, potentially reducing the   (1:400,000) in Milli-Q water was utilized.
            volume of secondary waste and increasing the efficiency
            of decontamination. 23,26-28                       2.3.2. Raman spectroscopy
              Given  the  current  global  context,  particularly   Raman spectra were acquired using a Horiba-Jobin-Yvon
            the escalation of wars and guerrilla activities, there   T64000 triple (Horiba Jobin-Yvon, Japan) spectrometer
            is a heightened risk of dirty bomb deployment and   equipped with a confocal attachment and a liquid nitrogen-
            increased vulnerability of nuclear power plants to cyber-  cooled CCD detector. A  green line (532.0  nm) from a
            attacks. This situation necessitates the consideration   solid-state laser (LAS-532-100-HREV [Q-BAIHE, China])
            of materials that can swiftly decontaminate surfaces   at 14 mW was used for excitation. The laser was focused
            exposed to radioactive substances, thereby facilitating   on the sample through an Olympus MPLN ×100 objective
            rapid reutilization of these areas. Accordingly, this study   lens, with the confocal attachment limiting the scattering
            assesses the potential of GQDs as a nanomaterial candidate   spot. Spectra collection was done in two modes: (i) at
            for the decontamination of surfaces contaminated with   various points on the sample surface and (ii) by altering
            radioactive materials.                             the position vertically centered on a particle.


            Volume 1 Issue 1 (2024)                         3                                doi: 10.36922/eer.3403
   80   81   82   83   84   85   86   87   88   89   90