| Literature DB >> 32366898 |
Hyunjin Cho1,2, Jun Hee Kim1,3, Jae Hun Hwang1,4, Cheol Sang Kim3,4, Se Gyu Jang1, Cheol Park5, Hunsu Lee6, Myung Jong Kim7.
Abstract
Research interest in boron nitride nanotubes (BNNTs) has increased after the recent success of large-scale BNNT syntheses using high-temperature-pressure laser ablation or high-temperature plasma methods. Nonetheless, there are limits to the application and commercialization of these materials because of the difficulties associated with their fine structural control. Herein, the growth kinetics of BNNTs were systemically studied for this purpose. The growth pressure of the nitrogen feed gas was varied while the growth temperature remained constant, which was confirmed by black body radiation measurements and calculations based on a heat loss model. Changing from the diffusion-limited regime to the supply-limited regime of growth kinetics based on the optimized BNNT synthesis condition afforded the control of the number of BNNT walls. The total amount of BNNTs possessing single and double walls was over 70%, and the BNNT surface area increased to 278.2 m2/g corresponding to small wall numbers and diameters. Taking advantage of the large surface area and high-temperature durability of the material, BNNTs utilized as a recyclable adsorbent for water purification. The efficiency of the BNNTs for capturing methylene blue particles in water was approximately 94%, even after three repetition cycles, showing the potential of the material for application in the filter industry.Entities:
Year: 2020 PMID: 32366898 PMCID: PMC7198605 DOI: 10.1038/s41598-020-64096-z
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.379
Figure 1Growth and analysis results of BNNTs synthesized by laser ablation (a) Schematic of the customized laser ablation system and laser incident on the molten boron ball of the boron fiber. (b) Images of the synthesized BNNTs in the chamber; A is an image from the high-speed camera, and B is the BNNTs synthesized at 14 bar. (c) Schematic of BNNT growth. (d) SEM image of BNNTs. (e) TEM image of SWBNNTs. (f) Raman spectrum of BNNTs. (g) EELS spectrum of BNNTs. (h,i) XPS spectra of BNNTs.
Figure 2Growth mechanism model and analysis of BNNTs (a) BNNT growth mechanism model (diffusion-limited regime and supply-limited regime). (b) Heat loss model of the molten boron ball. (c) Measured absolute temperatures of molten boron ball under different N2 pressures from 1 to 14 bar. (d) Photo images of BNNTs synthesized under different pressures (2, 4, 6, 8, 10, 12, and 14 bar). (e) Increased weight (%) after the oxidation of various samples. (f) TGA plots (weight, %) under different N2 pressures. (g) TGA plots (derivative weight, %/°C) under different N2 pressures.
Figure 3Comparison of BNNTs synthesized at 6 bar and 14 bar (a,b) TEM images of BNNTs synthesized at 6 bar and 14 bar. (c) TGA plot of BNNTs synthesized at 6 bar. (d,e) Numbers of BNNT layers synthesized at 6 bar and 14 bar. (f) TGA plot of BNNTs synthesized at 14 bar. (g) Table of numbers of BNNT layers synthesized at 6 bar and 14 bar. h BET analysis of BNNTs synthesized at 6 bar and 14 bar.
Figure 4Application of BNNTs as adsorbents to selectively capture MB (a) Scheme of the reaction between BNNTs and MB. (b) Photo images of the color change resulting from the changing concentration of MB from 10 min. to 180 min. (c) UV-vis absorption spectra of the solution. (d,e) Different C/C0 values for 6 bar BNNTs depending on time. (f) Recycling process of BNNTs through the simple annealing method to remove MB. (g) Percentages of MB captured depending on repeated usages.