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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

Postal Subscription Code 80-969

2018 Impact Factor: 2.809

Front. Chem. Sci. Eng.    2023, Vol. 17 Issue (7) : 840-852    https://doi.org/10.1007/s11705-022-2253-0
RESEARCH ARTICLE
Fabrication of recyclable Fe3+ chelated aminated polypropylene fiber for efficient clean-up of phosphate wastewater
Shangyuan Zhao1,2, Fangjia Wang3, Rui Zhou1,2, Peisen Liu1,2, Qizhong Xiong1,2, Weifeng Zhang1,2, Chaochun Zhang1,2, Gang Xu1,2(), Xinxin Ye1,2, Hongjian Gao1,2
1. Anhui Province Key Laboratory of Farmland Ecological Conservation and Pollution Prevention; Engineering and Technology Research Center of Intelligent Manufacture and Efficient Utilization of Green Phosphorus Fertilizer of Anhui Province, College of Resources and Environment, Anhui Agricultural University, Hefei 230036, China
2. Key Laboratory of JiangHuai Arable Land Resources Protection and Eco-restoration, Ministry of Natural Resources, College of Resources and Environment, Anhui Agricultural University, Hefei 230036, China
3. Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China
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Abstract

Herein, a Fe3+-loaded aminated polypropylene fiber has been reported as an efficient phosphate adsorbent. The remarkable phosphate removal ability of the fiber is due to Fe3+ immobilization, and it demonstrates a maximum adsorption capacity of 33.94 mg·P·g–1. Adsorption experiments showed that the fiber is applicable over a wide pH range from 2 to 9. Furthermore, the adsorption kinetics and isotherm data were consistent with the pseudo-second-order and Langmuir adsorption models, respectively. The adsorption equilibrium of the fiber for phosphate was reached within 60 min, indicating an efficient monolayer chemisorption process. Moreover, the adsorbent maintained prominent phosphate removal in the presence of competitive ions such as NO3 and Cl, exhibiting high selectivity. More importantly, the fiber demonstrated excellent reusability (5 times) and low adsorption limit below 0.02 mg·P·g–1. In addition, the phosphate removal efficiency of the fiber can exceed 99% under continuous flow conditions. The adsorption mechanism was studied by X-ray photoelectron spectroscopy, showing that the adsorption of phosphate on the fiber mainly depended on the chemical adsorption of the modified Fe3+. Overall, this study proves that the fiber possesses many advantages for phosphate removal, including high adsorption efficiency, lower treatment limit, good recyclability, and environmental friendliness.

Keywords phosphate adsorption      aminated polypropylene fiber      Fe3+      ligand exchange      reusability     
Corresponding Author(s): Gang Xu   
About author:

* These authors contributed equally to this work.

Online First Date: 17 January 2023    Issue Date: 05 July 2023
 Cite this article:   
Shangyuan Zhao,Fangjia Wang,Rui Zhou, et al. Fabrication of recyclable Fe3+ chelated aminated polypropylene fiber for efficient clean-up of phosphate wastewater[J]. Front. Chem. Sci. Eng., 2023, 17(7): 840-852.
 URL:  
https://academic.hep.com.cn/fcse/EN/10.1007/s11705-022-2253-0
https://academic.hep.com.cn/fcse/EN/Y2023/V17/I7/840
Fig.1  SEM images of (a) PPF, (b) PPAMF, (c) PPAMAF, (d) PPAMAF-Fe, and (e) PPAMAF-Fe-P; the image is magnified 200, 2000, and 20000 times.
Fig.2  FTIR spectra of (a) PPF, (b) PPAMF, (c) PPAMAF, (d) PPAMAF-Fe, and (e) PPAMAF-Fe-P.
Fig.3  XRD images of (a) PPF, (b) PPAMF, (c) PPAMAF, (d) PPAMAF-Fe, and (e) PPAMAF-Fe-P.
Fig.4  Effect of pH on phosphate adsorption capacity of PPAMAF-Fe.
Fig.5  (a) Phosphate adsorption kinetics of PPAMAF-Fe under different temperatures; (b) linear fitting diagram of first-order model; (c) linear fitting diagram of second-order model; (d) the linear equations of lnKc and 1/T and the linear equations of lnK2 and 1/T.
Fig.6  (a) Effect of phosphate concentrations on the phosphate removal capacity of PPAMAF-Fe; (b) linear fitting of the Langmuir isotherm model of PPAMAF-Fe for phosphate adsorption.
Fig.7  (a) Phosphate removal ability by PPAMAF-Fe in competitive ions solution; (b) breakthrough curves of phosphate solutions.
Fig.8  (a) EDS spectra of (I–V) PPF, PPAMF, PPAMAF, PPAMAF-Fe, and PPAMAF-Fe-P; (b) XPS survey of PPF, PPAMF, PPAMAF, PPAMAF-Fe, and PPAMAF-Fe-P; (c) high resolution spectrum of Cl 2p for PPAMAF-Fe; (d) high resolution spectrum of P 2p for PPAMAF-Fe-P; (e) high resolution Fe 2p spectrum of PPAMAF-Fe and PPAMAF-Fe-P; (f) high resolution N 1s spectrum of PPAMAF-Fe and PPAMAF-Fe-P.
Adsorbentsqe/(mg·P·g–1)Equilibrium timeRunRef.
Fe(III) loaded chitosan-biochar composite fibers19.24240 min[16]
Calcium-modified iron-based adsorbents (Fe/CaCl2)16.9720 min[58]
Crosslinked Fe(III)-chitosan (CTS-Fe-CL)10.20300 min5[17]
Fe(III)-doped chitosan (CTS-Fe)15.70300 min5[17]
Fe-La/MgO nanosheets12.2880 min[51]
Eggshell functionalized with iron oxyhydroxide21.98240 min[59]
microporous Fe2O3/g-C3N417.1115 min5[60]
PPAMAF-Fe34.4260 min5This study
Tab.1  Different iron modified adsorbents for phosphate removal
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