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Chinese Journal of Materials Research  2025, Vol. 39 Issue (9): 673-682    DOI: 10.11901/1005.3093.2024.336
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Preparation of Nano Ag0@ACF Material and Its Adsorption Performance for Gaseous Iodine
ZHAN Jie1, CHEN Xiaojiang2, ZOU Zhili3, SU Xingdong1, XIE Shiyu4, JIANG Liang2, WANG Jinling5, WANG Lielin2()
1.China Nuclear Power Technology Research Institute, Shenzhen 518028, China
2.Innovation Center of Nuclear Environmental Safety Technology, Southwest University of Science and Technology, Mianyang 621010, China
3.Yangjiang Nuclear Power Co., Ltd., Yangjiang 529500, China
4.CGN Cangnan Nuclear Power Co., Ltd., Wenzhou 325800, China
5.School of Chemical Engineering, Changchun University of Technology, Changchun 130012, China
Cite this article: 

ZHAN Jie, CHEN Xiaojiang, ZOU Zhili, SU Xingdong, XIE Shiyu, JIANG Liang, WANG Jinling, WANG Lielin. Preparation of Nano Ag0@ACF Material and Its Adsorption Performance for Gaseous Iodine. Chinese Journal of Materials Research, 2025, 39(9): 673-682.

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Abstract  

Radioactive gaseous iodine produced during the operation of nuclear reactors needs to be handled safely and efficiently. In this study, a nano-silver loading activated carbon fiber material Ag0@ACF was successfully synthesized by hydrothermal modification and in situ reduction methods, and then the Ag0@ACF material was characterized by SEM-EDS, XRD, BET, and XPS to evaluate the iodine adsorption performance of Ag0@ACF. The results show that the nano-silver particulates were uniformly loaded on the microporous activated carbon fiber material, the acquired Ag0@ACF composite exhibited high specific surface area and high reactivity. Its adsorption capacity of gaseous elemental iodine and methyl iodine reached 2.25 g/g and 0.48 g/g, respectively, the adsorption performance was increased by 2.5 times and 3.5 times in contrast to the blank activated carbon fiber material. With the increase of modifier concentration, the adsorption capacity of Ag0@ACF for gaseous iodine increases. The material still showed excellent adsorption performance (I2: 2.30 g/g, CH3I: 0.51 g/g) even at 130 oC. Through the analysis of material adsorption kinetics and mechanisms, the adsorption of Ag0@ACF materials for gaseous iodine is a chemical reaction between nano-silver and iodine to form a stable AgI, which is a stable chemical adsorption behavior. The highly reactive silver nanoparticles combined with the rich porous structure of activated carbon fiber materials can achieve rapid and efficient capture of gaseous iodine.

Key words:  inorganic non-metallic materials      radioactive gaseous iodine      Ag0@ACF      hydrothermal modification      in situ self-reduction      chemical adsorption     
Received:  15 August 2024     
ZTFLH:  TQ124.6  
Fund: National Natural Science Foundation of China(21101129);National Natural Science Foundation of China(41502028);Shenzhen Municipal Science and Technology Innovation Commission Key Technology R D Project(JSGG20200924171000001);Sichuan Province Natural Science Foundation(2022NSFSC0252);Announcement and Leadership Action Project(JBGS2024-431-004)
Corresponding Authors:  WANG Lielin, Tel: 15882867099, E-mail: wanglielin@swust.edu.cn

URL: 

https://www.cjmr.org/EN/10.11901/1005.3093.2024.336     OR     https://www.cjmr.org/EN/Y2025/V39/I9/673

Fig.1  Experimental setup diagram
Fig.2  SEM images of ACF (a) and Ag0@ACF composites (b), and the corresponding EDS-Mapping spectra of Ag0@ACF (c-f)
Fig.3  XRD patterns of ACF and Ag0@ACF
AdsorbentSpecific surface area / m2·g-1Pore volume /cc·g-1
ACF18160.842
1%Ag0@ACF15620.68
2%Ag0@ACF14030.642
3%Ag0@ACF12870.578
4%Ag0@ACF10950.492
5%Ag0@ACF9150.421
Table 1  Specific surface area and pore volume of Ag0@ACF
Fig.4  N2 adsorption and desorption curves (a), pore size distribution of ACF (b) and 5%Ag0@ACF (c)
Fig.5  Adsorption capacity of Ag0@ACF materials for elemental iodine (a) and methyl iodide (b)
Fig.6  Effect of adsorption time on the performance for elemental iodine (a) and methyl iodide (b)
AdsorbentAdsorption time / hAdsorption capacity of elemental iodine/methyl iodide / g·g-1
Th-UiO-66-MOFs[24]50.96/-
MOF membrane[25]360.6/-
NaY-NH4F-Bi2S3[26]100.49/-
Cu-BTC@PES[27]750.63/-
Cu0-SBA-15[12]10.95/-
ACF-TEDA[14]41.85/0.4
Ag0@ACF(this work)12.25/0.48
Table 2  Adsorption capacity of different adsorbent materials for gaseous iodine
Fig.7  Effect of temperatures on the adsorption performance for elemental iodine (a) and methyl iodide (b)
Fig.8  Quasi-first-order model fitting curves (a) and quasi-second-order model fitting curves (b) for elemental iodine adsorption, and quasi-first-order model fitting curves (c) and quasi-second-order model fitting curves (d) for methyl iodide adsorption
Adsorption kinetics of gaseous iodine on Ag0@ACFPseudo first-orderPseudo second-order
qeK1R2qeK2R2
I21.01230.0420.192.33041.74550.99
CH3I0.11470.52890.130.38302.32680.99
Table 3  Kinetic parameters of Ag0@ACF for gaseous iodine
Fig.9  SEM-EDS plots of adsorbed elemental iodine (a) and adsorbed methyl iodine (b)
Fig.10  Comparison of XRD diffraction of samples after adsorption of iodine (a), XPS energy spectrum of samples after adsorption of iodine (b), comparison of I 3d bimodal spectrum after adsorption of iodine (c) and comparison of Ag 3d bimodal spectrum after adsorption of iodine (d)
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