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- In relation to this article, we declare that there is no conflict of interest.
- Publication history
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Received July 17, 2024
Accepted December 11, 2024
Available online February 25, 2025
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This is an Open-Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/bync/3.0) which permits
unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.
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Efficient Removal of Hg 2+ from Wastewater by a Novel Cu-Modifi ed Attapulgite: Adsorption Performance and Mechanism
https://doi.org/10.1007/s11814-024-00360-6
Abstract
The development of low-cost and highly effi cient adsorbents is essentially needed for removing Hg 2+ species from desulfurization
sludge leaching wastewater. In this study, a series of novel Cu-modifi ed attapulgite (Cu–ATP) adsorbents were
synthesized via a simple HNO 3 treatment combined with an improved impregnation method. The Hg 2+ removal effi ciency
of these Cu–ATP adsorbents was investigated in simulated leaching wastewater. The eff ects of HNO 3 concentration, Cu
precursor, Cu-loading content, and other adsorption conditions on Hg 2+ removal using Cu–ATP were investigated. The
results demonstrated that Cu–ATP prepared with CuSO 4 as the precursor and treated with 3 mol/L HNO 3 showed excellent
Hg 2+ removal performance. Moreover, with increasing adsorbent content and adsorption time, the Hg 2+ removal effi ciency
of Cu–ATP fi rst increased and then stabilized. However, with an increase in pH value, the Hg 2+ removal effi ciency fi rst
increased and then decreased, whereas the removal showed a decreasing trend with increasing initial Hg 2+ concentration.
The adsorption kinetics results indicated that Hg 2+ adsorption on Cu–ATP was well described by the pseudo-second-order
model. Furthermore, various characterization methods, including Brunauer − Emmett − Teller analysis (BET), X-ray diff raction
(XRD), and X-ray photoelectron spectroscopy (XPS), were employed to analyze the physicochemical properties of the
adsorbents. The analyses confi rmed that the superior Hg 2+ removal effi ciency of Cu–ATP was mainly due to the complexation
of Hg 2+ with chemisorbed oxygen produced by Cu doping and S species generated from the Cu precursor (CuSO 4 ). These
fi ndings underscore the potential of Cu–ATP as a cost-eff ective adsorbent for removing Hg 2+ from wastewater.

