Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2021 Sep 26;14(19):5577.
doi: 10.3390/ma14195577.

Exploration of the Cs Trapping Phenomenon by Combining Graphene Oxide with α-K6P2W18O62 as Nanocomposite

Affiliations

Exploration of the Cs Trapping Phenomenon by Combining Graphene Oxide with α-K6P2W18O62 as Nanocomposite

Bangun Satrio Nugroho et al. Materials (Basel). .

Abstract

A graphene oxide-based α-K6P2W18O62 (Dawson-type polyoxometalate) nanocomposite was formed by using two types of graphene oxide (GO) samples with different C/O compositions. Herein, based on the interaction of GO, polyoxometalates (POMs), and their nanocomposites with the Cs cation, quantitative data have been provided to explicate the morphology and Cs adsorption character. The morphology of the GO-POM nanocomposites was characterized by using TEM and SEM imaging. These results show that the POM particle successfully interacted above the surface of GO. The imaging also captured many small black spots on the surface of the nanocomposite after Cs adsorption. Furthermore, ICP-AES, the PXRD pattern, IR spectra, and Raman spectra all emphasized that the Cs adsorption occurred. The adsorption occurred by an aggregation process. Furthermore, the difference in the C/O ratio in each GO sample indicated that the ratio has significantly influenced the character of the GO-POM nanocomposite for the Cs adsorption. It was shown that the oxidized zone (sp2/sp3 hybrid carbon) of each nanocomposite sample was enlarged by forming the nanocomposite compared to the corresponding original GO sample. The Cs adsorption performance was also influenced after forming a composite. The present study also exhibited the fact that the sharp and intense diffractions in the PXRD were significantly reduced after the Cs adsorption. The result highlights that the interlayer distance was changed after Cs adsorption in all nanocomposite samples. This has a good correlation with the Raman spectra in which the second-order peaks changed after Cs adsorption.

Keywords: Dawson-type polyoxometalate; cesium; graphene oxide; nanocomposite; sp2/sp3 carbon domain.

PubMed Disclaimer

Conflict of interest statement

There are no conflict to declare.

Figures

Figure 1
Figure 1
TEM imaging of (a) GOc70, (b) GOc72, and (c) GOc39 and SEM imaging of (d) GOc39, (e) GOc40, and SAED pattern from the location (A1,B1,C1) marked in pictures (ac), respectively.
Figure 2
Figure 2
SEM measurement: (a) [GO70POM]41, its EDS map (b) Tungsten element, (c) Oxygen element, (d) Carbon K-α X-ray element; TEM image: (e) [GO70POM]41, (f) GOc70, showing the formation of (a) layer after forming the composite [GO70POM]41 (E1) compared with the original GOC70 (F1) in the same-scale image (200 nm).
Figure 3
Figure 3
TEM image: (a) [GO40POM]41 after Cs adsorption, small black spots are identified (scale: 50 nm), (b) Elemental analysis of (a), (c) GOc70 after Cs adsorption, many small Cs clusters are seen (scale: 50 nm), (d) Elemental analysis of (c).
Figure 4
Figure 4
PXRD patterns of GOc70, GOc72, and their GO-POM nanocomposite before and after Cs adsorption.
Figure 5
Figure 5
Raman spectra before and after Cs adsorption for (a) GOc72 (b) [GO70POM]18.
Figure 6
Figure 6
The increment of Cs adsorption capacity (%) calculated by using the ratio before and after forming a composite in each GO sample.
Figure 7
Figure 7
TEM image of [GO70POM]18/Cs: (a) Aggregation after Cs adsorption, (b) Elemental analysis of (a).
Figure 8
Figure 8
IR spectra for (a) [GO70POM]18, (b) [GO70POM]18 after Cs adsorption, (c) [GO70POM]41, (d) [GO70POM]41 after Cs adsorption, (e) [GO40POM]18, (f) [GO40POM]18 after Cs adsorption, (g) [GO40POM]41, and (h) [GO40POM]18 after Cs adsorption.

Similar articles

Cited by

References

    1. Nishihara K., Yamagishi I., Yasuda K., Ishimori K., Tanaka K., Kuno T., Inada S., Gotoh Y. Radionuclide release to stagnant water in the Fukushima-1 nuclear power plant. J. Nucl. Sci. Technol. 2014;52:301–307. doi: 10.1080/00223131.2014.946455. - DOI
    1. Konings R.J.M., Wiss T., Beneš O. Predicting material release during a nuclear reactor accident. Nat. Mater. 2015;14:247–252. doi: 10.1038/nmat4224. - DOI - PubMed
    1. Uchida S., Tagami K. Soil-to-plant transfer factors of fallout 137Cs and native 133Cs in various crops collected in Japan. J. Radioanal. Nucl. Chem. 2007;273:205–210. doi: 10.1007/s10967-007-0737-5. - DOI
    1. Shizuma K., Fujikawa Y., Kurihara M., Sakurai Y. Identification and temporal decrease of 137 Cs and 134 Cs in groundwater in Minami-Soma City following the accident at the Fukushima Dai-ichi nuclear power plant. Environ. Pollut. 2018;234:1–8. doi: 10.1016/j.envpol.2017.11.018. - DOI - PubMed
    1. Koarashi J., Atarashi-Andoh M., Matsunaga T., Sato T., Nagao S., Nagai H. Factors affecting vertical distribution of Fukushima accident-derived radiocesium in soil under different land-use conditions. Sci. Total Environ. 2012;431:392–401. doi: 10.1016/j.scitotenv.2012.05.041. - DOI - PubMed

LinkOut - more resources