Journal of Inorganic Materials ›› 2025, Vol. 40 ›› Issue (4): 440-448.DOI: 10.15541/jim20240222
• RESEARCH LETTER • Previous Articles
LI Jianjun1,2,3(), CHEN Fangming1, ZHANG Lili3, WANG Lei1, ZHANG Liting2,3, CHEN Huiwen1, XUE Changguo1, XU Liangji1,2
Received:
2024-04-28
Revised:
2024-07-30
Published:
2025-04-20
Online:
2024-08-19
Contact:
LI Jianjun, professor. E-mail: ljj.hero@126.comAbout author:
LI Jianjun (1975-), professor. E-mail: ljj.hero@126.com
Supported by:
CLC Number:
LI Jianjun, CHEN Fangming, ZHANG Lili, WANG Lei, ZHANG Liting, CHEN Huiwen, XUE Changguo, XU Liangji. Peroxymonosulfate Activation by CoFe2O4/MgAl-LDH Catalyst for the Boosted Degradation of Antibiotic[J]. Journal of Inorganic Materials, 2025, 40(4): 440-448.
Fig. 2 SEM images of MgAl-LDH and CoFe2O4/MgAl-LDH, and EDS mappings of CoFe2O4/MgAl-LDH (a, b) SEM images of MgAl-LDH; (c, d) SEM images of CoFe2O4/ MgAl-LDH; (e) EDS scanning area; (f-j) EDS mappings of CoFe2O4/ MgAl-LDH
Fig. 6 Effects of different factors on TCH removal (a) Mass ratio of CoFe2O4 to MgAl-LDH; (b) Catalyst dosage; (c) PMS concentration; (d) pH ([TCH]=25 mg/L, [PMS]=1.5 mmol/L, CoFe2O4/MgAl-LDH=0.20 g/L, pH 7 and T=25 ℃)
Fig. 7 Effects of coexisting anions on TCH removal (a) and cyclic experiments (b) ([TCH]=25 mg/L, [PMS]=1.5 mmol/L, CoFe2O4/MgAl-LDH=0.20 g/L, pH 7 and T=25 ℃)
Fig. 8 Effects of ROS quenching tests on TCH removal (a) and EPR spectra of (b) DMPO-•OH and DMPO-SO4•−, (c) DMPO-O2•−, and (d) TEMP-1O2 ([TCH]=25 mg/L, [PMS]=1.5 mmol/L, CoFe2O4/MgAl-LDH=0.20 g/L, pH 7, T=25 ℃ and [Scavenger]=100 mmol/L)
Sample | SBET/(m2·g-1) | Pore volume/ (cm3·g-1) | Pore size/nm |
---|---|---|---|
CoFe2O4 | 35.42 | 0.15 | 10.76 |
MgAl-LDH | 138.78 | 0.16 | 5.76 |
CoFe2O4/MgAl-LDH | 82.84 | 0.25 | 23.26 |
Table S1 SBET and pore size analysis data of the prepared CoFe2O4, MgAl-LDH and CoFe2O4/MgAl-LDH
Sample | SBET/(m2·g-1) | Pore volume/ (cm3·g-1) | Pore size/nm |
---|---|---|---|
CoFe2O4 | 35.42 | 0.15 | 10.76 |
MgAl-LDH | 138.78 | 0.16 | 5.76 |
CoFe2O4/MgAl-LDH | 82.84 | 0.25 | 23.26 |
Catalyst | Tetracycline concentration/(mg·L-1) | Reactant conditions/(g·L-1) | Time/min | Degradation efficiency/% | Ref. |
---|---|---|---|---|---|
MIL-53(Fe)@AC | 20 | [catalyst]=0.20 [PMS]=2.00 | 120 | 92.4 | [S1] |
Fe-N/BC | 30 | [catalyst]=0.05 [PMS]=0.50 | 60 | 89.9 | [S2] |
Mn-MoS2@AABs | 20 | [catalyst]=0.40 [PMS]=2.50 | 90 | 82.4 | [S3] |
Co@N-MC | 25 | [catalyst]=0.04 [PMS]=0.20 | 30 | 91.2 | [S4] |
ZCO-CN | 20 | [catalyst]=0.13 [PMS]=0.10 | 30 | 91.0 | [S5] |
MIL-88A/CoFe2O4 | 10 | [catalyst]=0.25 [PMS]=1.00 | 60 | 90.0 | [S6] |
CoFe2O4/MgAl-LDH | 25 | [catalyst]=0.20* [PMS]=0.23* | 45 | 98.2 | This work |
Table S2 Comparison of the effects of different catalysts on degrading TCH
Catalyst | Tetracycline concentration/(mg·L-1) | Reactant conditions/(g·L-1) | Time/min | Degradation efficiency/% | Ref. |
---|---|---|---|---|---|
MIL-53(Fe)@AC | 20 | [catalyst]=0.20 [PMS]=2.00 | 120 | 92.4 | [S1] |
Fe-N/BC | 30 | [catalyst]=0.05 [PMS]=0.50 | 60 | 89.9 | [S2] |
Mn-MoS2@AABs | 20 | [catalyst]=0.40 [PMS]=2.50 | 90 | 82.4 | [S3] |
Co@N-MC | 25 | [catalyst]=0.04 [PMS]=0.20 | 30 | 91.2 | [S4] |
ZCO-CN | 20 | [catalyst]=0.13 [PMS]=0.10 | 30 | 91.0 | [S5] |
MIL-88A/CoFe2O4 | 10 | [catalyst]=0.25 [PMS]=1.00 | 60 | 90.0 | [S6] |
CoFe2O4/MgAl-LDH | 25 | [catalyst]=0.20* [PMS]=0.23* | 45 | 98.2 | This work |
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