2019
DOI: 10.1016/j.watres.2019.114997
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Transformation of tetracyclines induced by Fe(III)-bearing smectite clays under anoxic dark conditions

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Cited by 30 publications
(8 citation statements)
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“…When we employed three types of smectites (saponite, montmorillonite, and nontronite) with different Fe contents, a relatively high Glc consumption was achieved in proportion to the Fe content in the clay minerals (Figure S6). Although the Fe species in the structure participate in the dehydrogenation of Glc, the reaction proceeds even without Fe. The Lewis acidic site (an electron acceptor) has been suggested to correspond to the Al 3+ substituted by Si 4+ in the SiO 4 tetrahedral sheet of saponite (isomorphic substitution) .…”
Section: Resultsmentioning
confidence: 99%
“…When we employed three types of smectites (saponite, montmorillonite, and nontronite) with different Fe contents, a relatively high Glc consumption was achieved in proportion to the Fe content in the clay minerals (Figure S6). Although the Fe species in the structure participate in the dehydrogenation of Glc, the reaction proceeds even without Fe. The Lewis acidic site (an electron acceptor) has been suggested to correspond to the Al 3+ substituted by Si 4+ in the SiO 4 tetrahedral sheet of saponite (isomorphic substitution) .…”
Section: Resultsmentioning
confidence: 99%
“…To test the hypothesis that there is an underlying molecular-level mechanism explaining the pH-dependent Cu II -mediated oxidation of OTC, this study attempted to link pH-dependent speciation of Cu II –OTC complexes with the charge transfer rate k trans derived from the kinetics model of Cu I evolution. Previous studies have identified O3, N4, and O10 atoms of TCs as redox-active donor atoms which could be partially attacked by various electrophilic oxidant. ,,, Quite interestingly, preferentially coordinated tricarbonyl group (O3) at varying pH and additional coordinated dimethylamino group (N4) only at pH 8.5, which were identified by spectral analysis and corresponded with two kinds of site models, also participated into the complexation of Cu II –OTC, suggesting that O3 and N4 atoms as two Cu II -binding sites may be also the redox-active sites as the Cu II -mediated oxidation of OTC. To prove the above hypothesis, the correlation between the concentration of speciation of Cu II –OTC complexes and the charge transfer rate k trans at varying pH conditions were established (Figure ), which indicated that C [Cu II –H 2 L 0 ] at pH 3.0, C [Cu II –HL – ] at pH 5.0, and C [Cu II –L 2– ] at pH 8.5 performed a good linear correlation with k trans ,1 at corresponding pH and k trans ,2 at pH 8.5, i.e., C [speciation of Cu II –O3] was directly proportion to k trans ,1 but C [speciation of Cu II –N4] was inversely proportion to k trans ,2 .…”
Section: Resultsmentioning
confidence: 99%
“…Figure shows that the coordination modes between TCs and metals are various due to the differences in the binding sites of TCs and the properties of the metal ions. In studying their effects on abiotic transformations of antibiotics, redox-active transition metal ions have attracted researchers extensive interest and attention, especially for Fe III /Fe II and Cu II . Huang’s research group ,, conducted a systematic study on the Cu II -catalyzed transformation of organic pollutants, indicating that Cu II ion could play catalyzed oxidative or hydrolytic roles depending on different functional groups of Cu II -binding complexes and oxygen could reoxidize Cu I back to Cu II to enhance rapid degradation of TCs and β-lactam antibiotics .…”
Section: Introductionmentioning
confidence: 99%
“…It has been reported that some antibiotic molecules can complex with surface Fe(III) of iron minerals and that electron transfer within the complex induces the reduction of Fe(III) and the degradation of antibiotics. 28,29 It was presumed that TCs can play the same role as these organic molecules, promoting the generation of ROS and contributing to the oxidation of coexisting As(III). A recent study reported that TTC induced the reductive dissolution of ferrihydrite (Fe(II) release) and led to the release and oxidation of As(III) adsorbed by ferrihydrite in both aerobic and anaerobic conditions.…”
Section: Introductionmentioning
confidence: 99%