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Carbonate green rust

Titrate 0.1 M Fe" sulphate or chloride solution with M NaOH in a closed system and under N2 to pH 6.5-7 and then, while maintaining the pH by addition of M NaOH, slowly oxidize with a stream of C02-free air. Upon formation of a green precipitate (partial oxidation), separate this precipitate, still keeping it under N2 and freeze dry it (Schwertmann and Fechter, 1994 Lewis, 1997 Refait et ak, 1999). The preparation of a carbonate green rust is described by Taylor (1982) and Genin et ak (1998). [Pg.538]

Williams AGB, Scherer MM. Kinetics of chromate reduction by carbonate green rust. 220th National Meeting, Washington, DC, American Chemical Society 2000 42(2) 666-668. [Pg.421]

Fig. 13-1. Mossbauer spectrum of carbonate green rust recorded at 120 K and fitted to two Fe and two Fe doublets. Courtesy E. Murad (see Murad and Taylor, 1984). Fig. 13-1. Mossbauer spectrum of carbonate green rust recorded at 120 K and fitted to two Fe and two Fe doublets. Courtesy E. Murad (see Murad and Taylor, 1984).
Murad, E, and Taylor, R. M. (1984) The Mossbauer spectra of hydroxy carbonate green rust. Clay Min. 19 77-83. [Pg.174]

Composition, stabilization, and light absorption of Fe(II)Fe(III) hydroxy carbonate (green rust). 1086 ... [Pg.181]

Hamlaoui Y, Pedraza F, Tifouti L. Investigation of electrodeposited cerium oxide based films on carbon steel and of the induced formation of carbonated green rusts. Corros. Sd. 2008 50 2182-2188. DOI 10.1016/j.corsci.2008.05.017. [Pg.107]

Fig. 18.5), overlain by magnetite (Fig. 18.4 B), with goethite and lepidocrocite at the outer surface of the tubercle (Fig. 18.4A). The magnetite probably formed by oxidation of the green rust. In the interior of the older tubercles, magnetite was oxidized to maghemite. The carbonate form of green rust was also identified in the inner layers of rust tubercles in pipes for drinking water (Stampfl, 1969). Fig. 18.5), overlain by magnetite (Fig. 18.4 B), with goethite and lepidocrocite at the outer surface of the tubercle (Fig. 18.4A). The magnetite probably formed by oxidation of the green rust. In the interior of the older tubercles, magnetite was oxidized to maghemite. The carbonate form of green rust was also identified in the inner layers of rust tubercles in pipes for drinking water (Stampfl, 1969).
Green Rusts are not oxides or hydroxides in a strict sense but contain anions as an essential structural component. They consist of hexagonally close-packed layers of O and OH of the Fe(OH)2-structure type with Fe° and Fe in the interstices (Feitknecht and Keller, 1950). Fe gives the layer a positive charge which is balanced by intercalation of anions, such as chloride, sulfate, carbonate etc., between the layers. The sulfate and chlor-... [Pg.9]

Fig. 13-1 shows a Mossbauer spectrum of the carbonate form of green rust with two separate doublets fitted to both the Fe and Fe doublet. [Pg.144]

The black rust is covered by a very compact microporous layer, made up of green rust and calcium carbonates. This film influences the high-frequency loop of the impedance diagrams. [Pg.256]

In addition to the exclusion of carbon dioxide, it is necessary to exclude oxygen from reactions where cations of the metal hydroxide layer are easily oxidized under basic conditions. LDHs of this type include manganese, cobalt (131) and iron in the divalent oxidation state, and vanadium in the trivalent state. Reactions involving these metal ions have formed LDHs with, for instance, Co " /Co and Fe " /Fe metal content, with the latter, known as green rust, being discussed earlier in Section II.J. [Pg.392]

S.H. Drissi, Ph Refait, M. Abdelmoula, J.-M.R. Genin, Preparation and thermodynamic properties of Fe(II)-Fe(III) hydroxycarbonate (green rust 1), Pourbaix diagram of iron in carbonate-containing aqueous media. Cmros. Sci. 37, 2025-2041 (1995)... [Pg.175]

Green rust A greenish layer formed on iron surface. It contains iron oxyhydroxides. They may also contain carbonates and chlorides. [Pg.575]

Recent studies show that zero-valent metals (e.g., iron, zinc, and palladium), sulfide minerals (like FeS and FeS2), and green rust can act as abiotic agents and increase the reductive dechlorination rates of chlorinated ethanes and ethenes. For example, in the presence of zero-valent iron, P-elimination is the main degradation pathway of chlorinated ethenes. In the P-elimination pathway, chlorines in vicinal carbon atoms are eliminated and a third C-C bond will be formed (Tobiszewski and Namiesnik, 2012 Brown et al., 2009 and Ma and Wu, 2008). Kara et al. (2005) reported fliat with P-elimination, TCE, c-DCE, and t-DCE reduction occmred 40, 10, 100 times faster, respectively, in comparison to hydrogenolysis (Kara et al. 2005). [Pg.874]


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