TY - JOUR
T1 - Phosphate interactions with iron-titanium oxide composites
T2 - Implications for phosphorus removal/recovery from wastewater
AU - Cui, Jinli
AU - Yang, Jinsu
AU - Weber, Mischa
AU - Yan, Jia
AU - Li, Ruohong
AU - Chan, Tingshan
AU - Jiang, Yi
AU - Xiao, Tangfu
AU - Li, Xiaoyan
AU - Li, Xiangdong
N1 - Funding Information:
This study was supported by the National Natural Science Foundation of China ( 41977286 ), the Hong Kong RGC Theme-based Research Scheme (T21–711/16R), the Guangdong Key Research and Development Project ( 2019B110207002 ), Guangdong-Hong Kong-Macao Joint Laboratory for Environmental Pollution and Control (2019B121205006), the Natural Science Foundation of Guangdong Province ( 2019A1515011558 ), Earth Critical Zone and Eco-geochemistry ( PT252022024 ), and the Combined Foundation of Guangzhou City and University (College) for basic research projects ( 202102010391 ).
Publisher Copyright:
© 2023 Elsevier Ltd
PY - 2023/5/1
Y1 - 2023/5/1
N2 - Understanding the interactions between phosphate (P) and mineral adsorbents is critical for removing and recovering P from wastewater, especially in the presence of both cationic and organic components. To this end, we investigated the surface interactions of P with an iron-titanium coprecipitated oxide composite in the presence of Ca (0.5–3.0 mM) and acetate (1–5 mM), and quantified the molecular complexes and tested the possible removal and recovery of P from real wastewater. A quantitative analysis of P K-edge X-ray absorption near edge structure (XANES) confirmed the inner-sphere surface complexation of P with both Fe and Ti, whose contribution to P adsorption relies on their surface charge determined by pH conditions. The effects of Ca and acetate on P removal were highly pH-dependent. At pH 7, Ca (0.5–3.0 mM) in solution significantly increased P removal by 13–30% by precipitating the surface-adsorbed P, forming hydroxyapatite (14–26%). The presence of acetate had no obvious influence on P removal capacity and molecular mechanisms at pH 7. At pH 4, the removal amount of P was not obviously affected by the presence of Ca and acetate. However, acetate and high Ca concentration jointly facilitated the formation of amorphous FePO4 precipitate, complicating the interactions of P with Fe-Ti composite. In comparison with ferrihydrite, the Fe-Ti composite significantly decreased the formation of amorphous FePO4 probably by decreasing Fe dissolution due to the coprecipitated Ti component, facilitating further P recovery. An understanding of these microscopic mechanisms can lead to the successful use and simple regeneration of the adsorbent to recover P from real wastewater.
AB - Understanding the interactions between phosphate (P) and mineral adsorbents is critical for removing and recovering P from wastewater, especially in the presence of both cationic and organic components. To this end, we investigated the surface interactions of P with an iron-titanium coprecipitated oxide composite in the presence of Ca (0.5–3.0 mM) and acetate (1–5 mM), and quantified the molecular complexes and tested the possible removal and recovery of P from real wastewater. A quantitative analysis of P K-edge X-ray absorption near edge structure (XANES) confirmed the inner-sphere surface complexation of P with both Fe and Ti, whose contribution to P adsorption relies on their surface charge determined by pH conditions. The effects of Ca and acetate on P removal were highly pH-dependent. At pH 7, Ca (0.5–3.0 mM) in solution significantly increased P removal by 13–30% by precipitating the surface-adsorbed P, forming hydroxyapatite (14–26%). The presence of acetate had no obvious influence on P removal capacity and molecular mechanisms at pH 7. At pH 4, the removal amount of P was not obviously affected by the presence of Ca and acetate. However, acetate and high Ca concentration jointly facilitated the formation of amorphous FePO4 precipitate, complicating the interactions of P with Fe-Ti composite. In comparison with ferrihydrite, the Fe-Ti composite significantly decreased the formation of amorphous FePO4 probably by decreasing Fe dissolution due to the coprecipitated Ti component, facilitating further P recovery. An understanding of these microscopic mechanisms can lead to the successful use and simple regeneration of the adsorbent to recover P from real wastewater.
KW - Bimetal oxide composite
KW - Phosphorus
KW - Removal
KW - Surface complexation and precipitation
KW - Ternary complexes
UR - https://www.scopus.com/pages/publications/85150225802
U2 - 10.1016/j.watres.2023.119804
DO - 10.1016/j.watres.2023.119804
M3 - Journal article
C2 - 36889091
AN - SCOPUS:85150225802
SN - 0043-1354
VL - 234
JO - Water Research
JF - Water Research
M1 - 119804
ER -