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Environmental chemistry of soil

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ENVIRONMENTAL CHEMISTRY OF SOILS ENVIRONMENTAL CHEMJSTRY OF SOILS Murray B McBride :'\l"ew York Oxford OXFORD UNIVERSITY PRESS 1994 :.9 Oxford University Press Oxford New York Toronto Delhi Bombay Calcutta Madras Karachi Kuala Lumpur Singapore Hong Kong Tokyo Nairobi Dar es Salaam Cape Town Melbourne Auckland Madrid and associated companies in Berlin Ibadan Copyright © 1994 by Oxford University Press, Inc Published by Oxford University Press, Inc 198 Madison Avenue, New York, New York 10016-4314 Oxford is a registered trademark of Oxford University Press All rights reserved No part of this publication may be reproducted, stored in a retrieval system, or transmitted, in any form or by any means, electronic, mechanical, photocopying, recording, or otherwise, without the prior permission of Oxford University Press Library of Congress Cataloging-in-Publication Data McBride, Murray Environmental chemistry of soils / Murray McBride p em Includes index ISBN 0-19-507011-9 Soil chemistry I Title S592.5.M39 1994 631.4'I-dc20 93-1552 987654 Printed in the United States of America on acid-free paper TO JAN AND DEVIN 3.,.,d to the many generations of farmers in my family, '" ,·.hose inherited knowledge of the soil s not to be found in a book Preface -\n ordinary housefly, if placed within a hollow clear glass globe having a single hole for outlet, generally escapes rather promptly But a bee, under like circumstances, seldom :-[...]... equilibrium: (1.31) 1 A chemical component, i, of a system is any chemical species whose quantity can be varied independently of all other components ENVIRONMENTAL CHEMISTRY OF SOILS 14 The activity of a component i, given by ai, is defined in terms of chemical potentials: Ili = 117 + (1.32) RT In ai where 117 is the standard state chemical potential of i and R is the gas constant It can then be shown... (sultbydryl), R-S- ENVIRONMENTAL CHEMISTRY OF SOILS 18 soil Depending on the composition of the solution, a large fraction of the soluble metal ions in soil solutions may actually be complexed with inorganic or organic ligands For example, the toxic metal cadmium (CdH ) has a tendency to complex with as many as four Cl- ions The reactions can be written as four step-wise additions of one Cl- ligand,1... dwldt, the number of grams of molecules transferred across a boundary per second, the equation describing Fick's law of diffusion defines a diffusion coefficient, D: dw = _Da(dC) dt d.x (1.105) where dcl d.x is the concentration gradient and a is the cross-sectional area of the boundary The diffusion coefficient can be interpreted in terms of the equation ENVIRONMENTAL CHEMISTRY OF SOILS 28 D = RT 67rrNo'Y/... driving force The chemical potential of any chemical component, I i, of a system is the partial molar free energy: (1.30) where ni is the number of moles of component i in the system and nj is the number of moles of all other components In systems with several phases (a phase is defined as a chemically and physically uniform part of the system), the chemical potential of each component is equal in all... ~xample, the chemical reaction A + 2B- C ( 1.98) ENVIRONMENTAL CHEMISTRY OF SOILS 26 with a rate law of R = d[C] =k[A][BF dt If the concentration ofB is maintained at a high level such that [B] \ R ~ ( 1.99) » [A], then: k'[A] (1.100) and the reaction appears to be first-order This allows equation 1.97 to be used to determine the value of k' The simplified analysis of kinetics given here is only valid if the... calculated for a given temperature T and pressure P from the molecular properties of the system The molecular disorder of the system is measured by the entropy S, while the energy of the system is measured by E or H As the system undergoes reaction, these measures of disorder and energy change ENVIRONMENTAL CHEMISTRY OF SOILS 12 Weakly Hydrolysing r: 12 ~ La3 + Co • Mn2+ • Fe2 + Zn2+ Co2+ -~ Ni 2+... equal to half of the difference between the number of bonding and antibonding electrons For the hydrogen molecule, Hz, this is J1!(2 - 0) = 1 That is, the bond order is unity As bond order increases, the strength of the covalent bond increases Ionic Bonding This form of bondin{results if the outer valence electrons of two atoms, A and B, are of very different energies, so that transfer of one or more... ions with low charge (e.g., K+) The electric field of ions can induce dipole moments in uncharged, nonpolar molecules by distorting (polarizing) the electron distribution within the molecules ENVIRONMENTAL CHEMISTRY OF SOILS 6 WATER DIPOLE HYDRATED CATION HYDRATED ANION Figure 1.2 Separation of charge, q, for the H 2 0 dipole, and the orientation of these water dipoles around cations and anions in... those of the pure minerals For example, substitution of AI3+ into FeOOH appears to stabilize this mineral, resulting in a lower solubility product ENVIRONMENTAL CHEMISTRY OF SOILS 16 However, different structural forms, despite identical chemical compositions, can have different solubility products In the example given above, 10- 34 is the solubility product for gibbsite, one crystalline form of AI(OH)3'... necessary to the definition of thermodynamically exact quantities 1 The Debye-Huckel Model for Activity Coefficients In spite of the indifference of classical thermodynamics to the existence of ions, the quantification of soil chemical processes such as ion exchange requires that individual ion activities in solution at least be estimated This can be done using the Debye-Huckel theory of activities, which

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1. The powerful metal chelator, EDTA (ethylenediaminetetraacetic acid), is an efficient extracting agent for organically bound trace metal cations in soils at pH 6 and higher. The formation constants, K ML, for some metal-EDT A complexes in water are given below:Metal log KML Cu2+ 19.7 Ni2+ 19.5Zn2+ 17.2Cd2+ 17.5Ca2+ 11.5AIH 17.6Fe H 26.5(a) Why should EDT A be more efficient at extracting trace metals from neutral or alkaline soils than from acid soils?(b) The EDTA-extractable quantities of trace metals in soils amended with sewage sludges sometimes increase over a period of years. Can you propose a mechanism that would account for this change in the soil?(c) How would EDTA additions to a Ni-contaminated soil at pH 7 affect NiH activity, total soluble Ni, and Ni availability to plants Sách, tạp chí
Tiêu đề: KML "Cu2+
6. A calcareous soil, contaminated with a high level of copper, was found to contain the Cu hydroxycarbonate mineral, malachite. The solubility of malachite is defined by the disso- lution reaction:log K = 14.16(a) If the pH of this soil is 7.4, and the gas pressure of CO2 in the soil air is assumed to bePC02 = 10-2 atmospheres, calculate the activity of the Cu2+ ion in soil solution. (Ignore activity corrections for solution concentrations in this problem.)(b) Severe symptoms of Cu toxicity were observed in a corn crop grown in this soil. Does the answer in (a) provide a reliable indication that toxicity is likely to develop over a growing season?(c) How can the rhizosphere manipulate the activity of Cu2+ Sách, tạp chí
Tiêu đề: K "= 14.16 (a) If the pH of this soil is 7.4, and the gas pressure of CO2 in the soil air is assumed to be "PC02
3. Ferrous chloride, FeCI2, is known to be an effective soil amendment for lowering soluble levels of selenium in alkaline soils. Propose a reaction sequence that would explain this Khác
5. Given that AI3+ is not intrinsically a highly phytotoxic element (see Table 9.1), how can the widespread and common toxicity of Al to crops, especially in soils of the humid tropics, be explained Khác
8. In Chapter 7, Table 7.1, the reduction potentials of Mn02 and MnOOH are listed. Use the Nernst equation to determine if either of these Mn oxides in a soil solution at pH 7 would be able to generate chromate from precipitated Cr(OHh Assume that ion exchange limits Mn2+ solubility to 10- 5 M. What would be the significance of this reaction to the environ- ment?(Note: The relevant chromate-chromic half-cell reaction is:Eb = -0.13V) Khác

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