Phosphonate compounds are used in a wide variety of industrial and agricultural applications, and are commonly found in surface and ground waters. Adsorption to ferric hydroxide can have a significant effect on the transport and fate of phosphonate compounds in the environment. This research used density functional theory modeling to investigate the adsorption mechanisms of nitrilotris(methylenephosphonic acid) (NTMP) on ferric hydroxide. Standard Gibbs free energies of reaction (ΔG) and reaction activation barriers (E) were calculated for different possible adsorption mechanisms. Physical adsorption of NTMP to ferric hydroxide was promoted by negative charge assisted hydrogen bonding, and had ΔG ranging from -2.7 to -7.4 kcal/mol. NTMP was found to form three different types of inner sphere complexes, monodentate, bidentate mononuclear and bidentate binuclear. For the monodentate complexes, ΔG ranged from -8.0 to -13.7 kcal/mol, for the bidentate complexes ΔG ranged from -15.3 to -28.9 kcal/mol. Complexation with Ca decreased the energy for physical adsorption but increased the binding energies for mono- and bidentate complexes. Complexation with Ca also allowed formation of a tridentate ternary surface complex, whereby the Ca ion formed a bridge between three FeO and three PO groups. Physical adsorption had E = 0, but mono- and bidentate complex formation had E values ranging from 36 to 53 kcal/mol. Formation of tridentate ternary surface complexes involving Ca had the lowest activation barriers of 8 and 10 kcal/mol. The different activation barriers for different modes of adsorption may explain previous experimental observations of unusual kinetic behavior for adsorption and desorption of NTMP.
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http://dx.doi.org/10.1016/j.chemosphere.2017.02.015 | DOI Listing |
J Environ Sci (China)
July 2025
John A. Reif, Jr. Department of Civil and Environmental Engineering, New Jersey Institute of Technology, Newark, New Jersey 07102, USA.
In this study, synthetic wastewater containing 110 µg/L arsenate (As(V)), 0-20 mg/L fulvic acid (FA), and 0-12.3 mg/L phosphate was treated with 3 mg/L Fe. The mechanisms of FA and phosphate effects on As(V) removal by ferric chloride were determined using 0.
View Article and Find Full Text PDFAppl Biochem Biotechnol
December 2024
School of Metallurgy, Northeastern University, Shenyang, China.
Electrochemical and shake flask tests were used to examine the corrosion characteristics of typical gangue minerals in biometallurgical systems and their impact on microbial communities. The results show that the solubility order of the three gangue minerals is feldspar, mica, and quartz in descending order. Their corrosion processes are mainly controlled by cathodic electron-donating processes.
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November 2024
State Key Laboratory of Chemo/Biosensing and Chemometrics, Hunan University, Changsha, 410082, China. Electronic address:
Environ Sci Technol
November 2024
Institute for Building Materials, ETH Zürich, Laura-Hezner-Weg 7, 8093 Zürich, Switzerland.
The formation of energetically favorable and metastable mineral phases within the Fe-HO system controls the long-term mobility of iron complexes in natural aquifers and other environmentally and industrially relevant systems. The fundamental mechanism controlling the formation of these phases has remained enigmatic. We develop a general partial equilibrium model, leveraging recent synchrotron-based data on the time evolution of solid Fe(III) hydroxides along with aqueous complexes.
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September 2024
School of Water Conservancy and Environment, University of Jinan, Jinan, 250022, China.
Vertically oriented interstitial atom carbon-anchored molybdenum disulfide (C-MoS) nanospheres loaded with iron oxyhydroxide (β-FeOOH) were proposed for modulating the surface catalytic activity and stability of the unsaturated catalytic system. The β-FeOOH@C-MoS efficiently activated peroxymonosulfate (PMS) to degrade 95.4% of tetracycline (TC) within 30 min, owing to the more sulfur vacancies, higher surface hydroxyl density, redox ability and electronic transmission rate of β-FeOOH@C-MoS.
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