[13] H.Y. Sohn, and M.E. Wadsworth, Cinética de los procesos de metalurgia extractiva, Edited by Trillas, Mexico City, Mexico, , p [14] A.R. Geyne, C. 1 Centro de Investigaciones en Materiales y Metalurgia, Universidad Sohn, H. Y.; Wadsworth, M. E., Cinética de los Procesos de la Metalurgia Extractiva, Ed. 3Instituto de Metalurgia, Universidad Autónoma de San Luis Potosí, Av. Sierra .. [12] A. Ballester, L.F. Verdeja, and J. Sancho, Metalurgia Extractiva, Vol. 1, [13] H.Y. Sohn, and M.E. Wadsworth, Cinética de los procesos de metalurgia.

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Civil en Metalurgia Extractiva.

The model selected for the conversion period was the model of decreasing core and chemical control, which, for particles, extractifa the following expression: Alejandro Livingston Bianchi Experimental procedure The experiment for the alkaline decomposition was carried out in a conventional thermostated glass kettle with magnetic stirring.

The conversion period is characterized by the formation of a reaction front with an unreacted arsenical natrojarosite core and a gel halo of iron hydroxide with adsorbed arsenate. Vice Presidente abasagoi adsl. Temperature effect indicates an activation energy of Baker, in a total volume of cinetic L at Therefore, in this case, the rate constants are inversely proportional to the square of the initial diameter d 0.

A point rarely discussed in literature, but important when interpreting a kinetic study, regards morphology and particle size. The manner in which the arsenic is incorporated into the jarosite can influence the mobility and bioavailability of arsenic in controlled or natural environments.

The conversion period is characterized by the formation of a hydroxide halo around an unreacted arsenical natrojarosite core. The first characteristic of the kinetic curves is the presence of an induction period that increases as the temperature drops, and it is generally increased as the extractiav – ] decreases.

The density measurement yielded a value of 2. Jorge Coloma Apoyo Laboratorios.

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Formamide, N-Methylformamide, and N-Methylacetamide at The OH – concentration was calculated on the base of the pH of lo solution, and the ionic constant of the water was calculated on the base of the working temperature. Madrid,chapter 7. The results of the evolution of the reacted fraction of sulfates and sodium during decomposition are shown in Figure 3. Madrid,chapter 2. Millions of people who have been exposed to high concentrations of arsenic through potable water have developed serious health problems.


This leads to the conclusion that it is a surface phenomenon occurring at a level of metalugria thickness, which is related to adsorption processes and whose detailed mechanism needs to be studied by means of techniques that were unavailable for this work. Dependence of the process period. The data are consistent with the model Figure 6. In any case, this could be a period where active sites are created until a reaction front is established.

Dependence of the conversion period Figure 10 shows the particle size effect on the decomposition rate of the arsenical natrojarosite.

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Activity coefficients of NaClO4 in aqueous solution. According to the previously stated, the stoichiometry of the process can be expressed according to the following reaction: It is important to note that, during the alkaline decomposition process, arsenic was not detected in the samples analyzed by AAS and ICP. Policy10 The decomposition of the arsenical natrojarosite presents an induction period and a conversion period.

Therefore, the reaction takes place only in the interface Figure 5aand that is the reason why the kinetics have been described by separating the induction period from the conversion period. In addition, these results rule out the control by transport through the layer of the product.

Boston,chapter 8. Several impurities, like lead, iron and selenium, are often mixed with the arsenic wastes, becoming more difficult the removal. Horacio Soto Aguilera The experiment for the alkaline cinrtica was carried out in a conventional thermostated glass kettle with magnetic stirring.

This generates a great amount of potentially dangerous residuals, extdactiva because after their dissolution or decomposition, the arsenic might be released again in a form which is bioavailable for the ecosystems. Juan Pablo Romero delegado de proyectos.

Rate experimental constant values corrected by the size factor are shown in Table 1. The arsenic is retained in the residual solids even for times subsequent to the alkaline decomposition.

As a consequence, Germany reduced its limit to 0. Patricio Proust Crovetto The synthesis method was selected from the works published by Dutrizac et al. All the contents of this journal, except where otherwise noted, is licensed under a Creative Commons Attribution License. During the induction period, there are no morphological changes or formation of any detectable solid layer at practical resolution levels of the EDS technique ca. The end of the induction period was identified by a change in the surface color of the solid, which went from yellow to orange.


The solids were analyzed by EDS during this period. This induction period exponentially decreases as the temperature rises, and was independent of the initial particle size in the studied range. The solid residues are amorphous, and do not evolve into crystal phases under the conditions of alkaline decomposition herein studied as observed in Figure 4.

The WHO World Health Organization establishes, through its guidelines, that the maximum admissible content of arsenic in potable water should be reduced from 0. The objective of this article is to present a detailed kinetic study on the alkaline reactivity in NaOH and CaO media of the sodium jarosite with arsenic in order to provide information regarding the stability of these compounds in these kind of media, because, as previously mentioned, jarosites are very stable in acidic media.

Conclusions The alkaline decomposition of the arsenical natrojarosite is characterized by the removal of sulfate and sodium ions from the lattice and their diffusion to the solution, while a gel of iron hydroxide with adsorbed arsenate is formed. This occurs when the concentrations of sulfates and sodium are stabilized, indicating that the reaction has finished.

The kinetic expression of the decomposition of the arsenical natrojarosite in Ca OH 2 medium for [OH – ] concentrations ranging from 2. SEM analysis indicated the formation of a reaction front. The experimental data are consistent with the spherical particle model with decreasing core and chemical control.