Magnetic MXene-NH2 decorated with persimmon tannin for highly efficient elimination of U(VI) and Cr(VI) from aquatic environment
Introduction
The rapid development of economy has created serious pollution of water body by various industrial pollutants, which brings a severe adverse impact on nature and living organisms [1]. Among these contaminants, uranium and chromium have attracted particular attentions. Uranium is an important raw material for nuclear power generation, which generally exists in contaminated water in the form of stable U(VI). Owing to its high stability, migration and radioactivity, hitherto the efficient treatment of uranium pollution in water still remains challenging [2]. On the other hand, Cr(VI) ions mainly exist as anions (HCrO4−, CrO42− and Cr2O72−) in water environment, which are easily migrated, absorbed and accumulated in organism [3]. To safeguard water sources, it is urgent to develop highly efficient approach for elimination of uranium or chromium-contaminated from aquatic environment. Current remediation technologies for removal of these hazardous pollutants from wastewater include ultra-filtration [4], catalytic reduction [5], chemical precipitation [6] and adsorption [7]. Comparatively speaking, adsorption is considered as the most convenient and effective method in water pollution control due to its advantages in low energy consumption, ease of operation and cheap cost. So far, many kinds of different adsorbents, which including mesoporous carbons [8], hydrotalcite [9], SiO2 [10], Fe3S4 [11], and so forth, have been studied to eliminate the two classic contaminants from water environments. However, the drawbacks of these traditional adsorbents can be obvious because of their high cost in regeneration, limited adsorption amounts and the hazard they cause to both the environment and practitioners. Hence, developing novel materials for water environmental purification is a task that must be pursued indefinitely.
MXenes are a family of two-dimensional (2D) transition-metal carbides and nitrides, its molecular structure is composed of transition metals (such as Ti, V, Nb, etc.) and carbon/nitrogen [12]. 2D MXenes have captured widespread attention in the environmental pollution remediation due to their high surface-volume ratio, unique inter-layer structure and abundant active functional groups. For instance, Kong et al. [13] developed an amino-functionalized MXenes for efficient removal of Cr(VI), and the experimental results found that amino groups and Ti3C2Tx nanosheets exhibited synergistic effects in the adsorption-reduction of Cr(VI). Zhang et al. [14] synthesized a carboxyl functionalized MXene nanosheets to elimination of uranyl ion from radioactive wastewater, and this adsorbent showed excellent removal ability for U(VI) with a high maximum adsorption amounts. Feng et al. [15] fabricated a MXene/PEI functionalized sodium alginate aerogel using a simple way, and this material exhibited an excellent ability to capture Cr(VI), and still maintained a high removal rate after five cycles. He et al. [16] investigated the adsorption efficiency of three-dimensional (3D) porous MXene gel towards uranium(VI), and this MXenes gel sorbent exhibited an excellent adsorption for uranium(VI) because of its 3D porous structure and abundant adsorption active sites. Nevertheless, while these MXenes based materials exhibited superior performance for targeted contaminants, they still existed some deficiencies during enrichment processes. Recent studies have pointed out that the narrow interfloor distance of MXenes is not beneficial to mass transfer and diffusion of target pollutants. Meanwhile, the insufficient of adsorption sites with special recognition function at the surface or interlayer of MXenes, which may result in poor selectivity to target pollutants. What's more, the separation and recycling of these MXenes materials from wastewater are still a challenging. Thus, it is imperative to exploit a fresh approach to construct a new type of MXenes materials for elimination of contaminants from water environment.
It is well known that natural organic matters are a primary electron source for metal ions adsorption-reduction in natural soils and waters [17]. Indeed, persimmon tannins are also an important category of natural organic matters, which is produced from the juice of young astringent persimmons after fermentation. More importantly, persimmon tannin is also a biological macromolecule, its molecular weight range is 7–20 kDa and the polymerization degree is 19–47 [18], [19], which have been applied as natural coagulants for adsorption and immobilization of inorganic or organic contaminants from wastewater. Meanwhile, the abundant adjacent hydroxyl groups with chelating ability, combined with an easy conversion into a solid materials make tannins good precursors for bio-adsorbents [20]. Moreover, magnetic nanoparticles have been intensively studied, not only for scientific interest, but also for technological applications. Particularly, Fe3O4 nano-particles have aroused considerable interest because they can help pollutant-loaded adsorbent to efficient separate from wastewater system by the extra magnet [21]. Based on the above considerations, it is of great significance to combine the advantages of MXenes, tannin and Fe3O4 to construct a new composite materials.
The aims of this investigation were as follows: (1) the influencing factors such as pH value, reaction time and concentration on removal efficiency were studied in detailed by batch experiments; (2) the classical kinetics, isotherms and thermodynamic formulas were taken into account to explore the interfacial reaction process between the adsorbates and adsorbents; (3) the relationship between the structural features and absorption properties of Fe3O4@Ti3C2-NH2-PT was evaluated; (4) the reaction mechanism between the targeted pollutants and Fe3O4@Ti3C2-NH2-PT was analyzed by the spectral analysis. Consequently, this magnetic persimmon tannin-functionalized MXenes was expected to be used in water purification and environmental remediation.
Section snippets
Materials
The single-layer Ti3C2-NH2 and persimmon peel were supplied by Chengdu Chron Chemicals Co, Ltd. (Chengdu, China). The ammonium hydroxide (NH3∙H2O, 26–28 wt%), ferric chloride hexahydrate (FeCl3.6H2O, 98 wt%), glutaraldehyde (GA, 50 wt%) and iron sulfate heptahydrate (FeSO4.7H2O, 98 wt%) were supplied from Shanghai Titan Technology Co., Ltd. The uranium and chromium ions standard solutions were prepared by dissolving uranyl nitrate hexahydrate (UO2(NO3)2.6H2O, 99 wt%) and potassium dichromate (K2
Morphology and structure analysis
The morphologies and microstructure of the as-prepared samples were characterized by electron microscope technique. In Fig. 2a, one can see that Ti3C2-NH2 exhibited a lamellar and densely stacked morphology with a lateral size of 0.5–3 μm. However, the samples of Ti3C2-NH2-PT were relatively rough and irregular structure after cross-linking reaction (Fig. 2b), which may be due to the persimmon tannin were successfully introduced into the surface of MXenes layers [24]. More importantly,
Conclusion
In conclusion, a novel magnetic MXenes based composite was successfully constructed and applied for elimination of two metal ions from the simulated contaminated water. Advanced characterization analysis demonstrated that abundant phenolic hydroxyl groups and Fe3O4 particles existed on the surface of Fe3O4@Ti3C2-NH2-PT, which resulted in improved electronic carriers and high separation efficiency. The systematic adsorption experiments determined that Fe3O4@Ti3C2-NH2-PT exhibited exceptionally
CRediT authorship contribution statement
Fenglei Liu: Investigation, Data curation, Writing-original draft. Jinru Hu: Investigation, Project administration. Baowei Hu: Writing-review & editing.
Acknowledgment
We gratefully thank the China Postdoctoral Science Foundation (2021M702911), the Zhejiang Public Welfare Technology Application and Social Development Project (LGF21C030001) and the Key Laboratory of Environmental Pollution Control Technology Research of Zhejiang Province (No. 2021ZEKL12).
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