Kinetics and Mechanism of the Reaction of Hydrogen Sulfide with Lepidocrocite
The initial reaction between hydrogen sulfide and the surface of lepidocrocite was studied in the pH range between 4 and 8.6 by monitoring the change of the emf of a pH2S sensor. The rate of H2S oxidation is pseudo first order with respect to H2S and shows a strong pH dependence with a maximum at pH...
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1992
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| LEADER | 06606caa a22008297a 4500 | ||
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| 001 | PAPER-12657 | ||
| 003 | AR-BaUEN | ||
| 005 | 20230518204250.0 | ||
| 008 | 190411s1992 xx ||||fo|||| 00| 0 eng|d | ||
| 024 | 7 | |2 scopus |a 2-s2.0-0027092560 | |
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 100 | 1 | |a Stefan, P. | |
| 245 | 1 | 0 | |a Kinetics and Mechanism of the Reaction of Hydrogen Sulfide with Lepidocrocite |
| 260 | |c 1992 | ||
| 270 | 1 | 0 | |m Stefan, P.; CH-6047 Kastanienbaum, Depto de Química Inorgánica, Analítica y Química Física, Facultad de Ciencias Exactas y Naturales, Ciudad Universitaria Pabellón II, Buenos Aires, Argentina 1428, United States |
| 506 | |2 openaire |e Política editorial | ||
| 504 | |a Einsele, W., (1936) Arch. Hydrobiol., 29, p. 664 | ||
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| 504 | |a Tessier, A., Carignan, R., Dubreuil, B., Rapin, F., (1989) Geochim. Cosmochim. Acta, 53, p. 1511 | ||
| 504 | |a Belzile, N., Tessier, A., (1990) Geochim. Cosmochim. Acta, 54, p. 103 | ||
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| 504 | |a Nealson, K.H., (1983) Microbial Geochemistry, , Krumbein, W.E., Ed.; Blackwell: Oxford, England | ||
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| 504 | |a Stumm, W., Wieland, E., (1990) Aquatic Chemical Kinetics-Reaction Rates of Processes in Natural Waters, , John Wiley & Sons: New York | ||
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| 504 | |a Schwertmann, U., Taylor, R.M., (1989) Minerals in the Soil Environment, , 2nd ed.; Dixon, J.B., Ed.; Soil Science Society of America: Madison, WI | ||
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| 504 | |a Peters, K., Huber, G., Netsch, S., Frevert, T., (1984) GWT, Gas-Wasserfach: Wasser/Abwasser, 125, p. 386 | ||
| 504 | |a Hering, J.G., Stumm, W., (1990) Mineral Water-Interface Geochemistry; Reviews in Mineralogy 23, , Hochella, M.F., White, A.F., Eds.; Mineralogical Society of America: Washington, DC | ||
| 504 | |a Baumgartner, E., Blesa, M.A., Maroto, A.J.G., (1982) J. Chem. Soc., Dalton Trans., 9, p. 1649 | ||
| 504 | |a Cornell, R.M., Schindler, P.W., (1987) Clays Clay Miner., 33, p. 347 | ||
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| 504 | |a Luther, G.W., III, (1990) Aquatic Chemical Kinetics-Reaction Rates of Processes in Natural Waters, , Stumm, W., Ed.; John Wiley & Sons: New York | ||
| 504 | |a Ben-Yaakov, S., (1973) Limnol. Oceanogr., 18, p. 86 | ||
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| 504 | |a Urban, N., Environmental Chemistry of Lakes and Reservoirs, , Baker, L.A., Ed.; ACS Advances in Chemistry Series; American Chemical Society: Washington, DC, in press | ||
| 520 | 3 | |a The initial reaction between hydrogen sulfide and the surface of lepidocrocite was studied in the pH range between 4 and 8.6 by monitoring the change of the emf of a pH2S sensor. The rate of H2S oxidation is pseudo first order with respect to H2S and shows a strong pH dependence with a maximum at pH 7. Two rate laws were derived: R(5<pH<6) = ka[H+]-2[H2S]tot,A and R(7<PH<8.6) = Kb[H+]1[H2S]totA with ka = 1.5 × 10-13 M2 min-1 and kb = 2 X 106 M-1 min-1. The pH maximum of the reaction rate can be explained by using a surface speciation model suggested for the reductive dissolution of hematite by H2S (1): The oxidation rate of H2S is proportional to the concentration of inner-sphere surface complexes of HS- formed with either the neutral ferric oxide surface sites (>FeOH) or the protonated ferric oxide surface sites (>FeOH2+). The amount of protons consumed per mole of H2Stot suggests that polysulfides and elemental sulfur are the initial products formed during the experiments. © 1992, American Chemical Society. All rights reserved. |l eng | |
| 593 | |a CH-6047 Kastanienbaum, Depto de Química Inorgánica, Analítica y Química Física, Facultad de Ciencias Exactas y Naturales, Ciudad Universitaria Pabellón II, Buenos Aires, Argentina 1428, United States | ||
| 690 | 1 | 0 | |a FERRIC HYDROXIDE |
| 690 | 1 | 0 | |a HYDROGEN SULFIDE |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a CHEMICAL ANALYSIS |
| 690 | 1 | 0 | |a CHEMICAL REACTION KINETICS |
| 690 | 1 | 0 | |a LAKE |
| 690 | 1 | 0 | |a OXIDATION |
| 690 | 1 | 0 | |a WATER POLLUTANT |
| 690 | 1 | 0 | |a WATER TREATMENT |
| 650 | 1 | 7 | |2 spines |a PH |
| 700 | 1 | |a Marla Dos, S.A. | |
| 700 | 1 | |a Bernhard, W. | |
| 700 | 1 | |a Rene, G. | |
| 773 | 0 | |d 1992 |g v. 26 |h pp. 2408-2413 |k n. 12 |p Environ. Sci. Technol. |x 0013936X |w (AR-BaUEN)CENRE-14 |t Environmental Science and Technology | |
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| 856 | 4 | 0 | |u https://doi.org/10.1021/es00036a011 |y DOI |
| 856 | 4 | 0 | |u https://hdl.handle.net/20.500.12110/paper_0013936X_v26_n12_p2408_Stefan |y Handle |
| 856 | 4 | 0 | |u https://bibliotecadigital.exactas.uba.ar/collection/paper/document/paper_0013936X_v26_n12_p2408_Stefan |y Registro en la Biblioteca Digital |
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| 999 | |c 73610 | ||