Contrasting effects of a traditional material of polyaluminum chloride and an emerging material of lanthanum carbonate capping on sediment internal phosphorus immobilization

Qi Li; Wenming Yan; Minjuan Li; Xiang Chen; Tingfeng Wu; Xiangyu He; Qi Yao; Yulin Yan; Gaoxiang Li

doi:10.1016/j.scitotenv.2024.170538

Contrasting effects of a traditional material of polyaluminum chloride and an emerging material of lanthanum carbonate capping on sediment internal phosphorus immobilization

Sci Total Environ. 2024 Mar 20:917:170538. doi: 10.1016/j.scitotenv.2024.170538. Epub 2024 Feb 1.

Authors

Qi Li¹, Wenming Yan², Minjuan Li³, Xiang Chen⁴, Tingfeng Wu⁵, Xiangyu He⁶, Qi Yao⁶, Yulin Yan⁶, Gaoxiang Li⁶

Affiliations

¹ College of Hydrology and Water Resources, Hohai University, Nanjing 210098, China; National Key Laboratory of Water Disaster Prevention, Hohai University, Nanjing 210098, China.
² College of Hydrology and Water Resources, Hohai University, Nanjing 210098, China; National Key Laboratory of Water Disaster Prevention, Hohai University, Nanjing 210098, China. Electronic address: ywm0815@163.com.
³ National Key Laboratory of Water Disaster Prevention, Hohai University, Nanjing 210098, China.
⁴ Nanjing Institute of Environmental Sciences, Ministry of Ecology and Environment, Nanjing 210042, China.
⁵ State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China.
⁶ College of Hydrology and Water Resources, Hohai University, Nanjing 210098, China.

PMID: 38296068
DOI: 10.1016/j.scitotenv.2024.170538

Abstract

Polyaluminum chloride (PAC) is a traditional material used for immobilizing sediment internal phosphorus (P) in field-scale experiment. Lanthanum carbonate (LC) is an emerging material which have been used in immobilizing sediment internal P in laboratory. To promote LC in practice, the premise is that it does have advantages over traditional material when used. Herein, a 90-day incubation experiment was conducted comparing the effectiveness and mechanism of LC and PAC capping in controlling sediment internal P. The results of isotherm experiment and XPS analysis indicated that the adsorption mechanism of P onto LC and PAC involved ligand exchange and formation of inner-sphere La/Al-O-P complexes. The incubation experiment revealed that PAC capping was more effective in reducing pore water soluble reactive phosphorus (SRP), exhibiting a reduction of up to 81.32 % but showed a decrease trend. However, LC capping resulted in a reduction of pore water SRP up to 52.84 % and maintained stability. On average, LC and PAC capping reduced SRP flux by 0.27 and 0.32 μg·m^-2d^-1, respectively relative to the control sediment. Moreover, LC capping facilitated the formation of Fe(III)/Mn(IV) oxyhydroxides, leading to an increased P adsorption, whereas PAC capping facilitated the reduction of Fe(III)/Mn(IV) minerals with P release. Additionally, LC capping resulted in the reduction of a higher ratio of mobile P/TP to stable P forms than PAC capping, as compared to the control. In contrast to PAC capping which converted mobile P to stable NaOH-rP, LC capping transformed mobile P and NaOH-rP into more stable HCl-P and ResP. Both LC and PAC capping caused variations in sediment bacterial communities. Nevertheless, PAC capping heightened the risk of Co, Ni, Cu, and Pb releases in sediment compared to LC capping. In summary, this study suggested that LC capping surpassed PAC capping in immobilizing sediment internal P.

Keywords: Heavy metals; Lanthanum carbonate; Microorganisms; Phosphorus; Polyaluminum chloride; Sediment.