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Interaction of Fluazifop with Al-, Fe3+-, and Cu2+-Saturated Montmorillonite

Published online by Cambridge University Press:  02 April 2024

G. Micera
Affiliation:
Dipartimento di Chimica, Università di Sassari, Via Vienna 2, 07100 Sassari, Italy
A. Pusino
Affiliation:
Istituto di Chimica Agraria, Università di Sassari, Via E. de Nicola 10, 07100, Sassari, Italy
C. Gessa
Affiliation:
Istituto di Chimica Agraria, Università di Sassari, Via E. de Nicola 10, 07100, Sassari, Italy
S. Petretto
Affiliation:
Istituto di Chimica Agraria, Università di Sassari, Via E. de Nicola 10, 07100, Sassari, Italy
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Abstract

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The adsorption of the pesticide Fluazifop, (RS)-2-[4-[[(5-trinuoromethyl)-2-pyridin-yl]oxy]phenoxy] propanoic acid, on homoionic Cu2+-, Fe3+-, and Al-bentonites was investigated by infrared and electron spin resonance spectroscopy. For comparison, the binary complexes of the acid containing the above ions were prepared and characterized. On the whole, the results show that the interaction of the acid with the clay may have involved both the protonation of the pyridine nitrogen atom, due to a proton transfer from the acid metal-bound water, and the formation of direct bonds between the carboxylate groups and the exchange cations. The extent of these interactions was dependent on the nature of the metal ions, the Cu ions being more effective in producing CHCl3-extractable neutral carboxylate complexes, while Al and Fe favored the formation of species bearing protonated nitrogen atoms and un-dissociated carboxyl groups.

Type
Research Article
Copyright
Copyright © 1988, The Clay Minerals Society

References

Bewick, D. W., 1986 Stereochemistry of Fluazifop-butyl transformations in soil Pest. Sci. 17 349356.CrossRefGoogle Scholar
Brown, G. M. and Chidambaram, R., 1973 Dinuclear copper(II) acetate monohydrate: A redetermination by neutron-diffraction analysis Acta Cryst. B29 23932403.CrossRefGoogle Scholar
Carr, J. E., 1986 The uptake, translocation and metabolism of Fluazifop-butyl Pestic. Sci. 17 5864.Google Scholar
Carter, D. L., Heilman, M. D. and Gonzales, C. S., 1965 Ethylene glycol monoethyl ether for determining surface area of silicate minerals Soil Sci. 100 356360.CrossRefGoogle Scholar
Cook, D., 1961 Vibrational spectra of pyridinium salts Can. J. Chem. 39 20042024.CrossRefGoogle Scholar
Farmer, V. C. and Mortland, M. M., 1966 An infrared study of the coordination of pyridine and water to exchangeable cations in montmorillonite and saponite J. Chem. Soc. A 344351.CrossRefGoogle Scholar
GESSA, C. PUSINO, A. SOLINAS, V. and PETRETTO, S., 1987 INTERACTION OF FLUAZIFOP-BUTYL WITH HOMOIONIC CLAYS Soil Science 144 6 420424.CrossRefGoogle Scholar
Mortland, M. M. and Bailey, S. W., 1975 Interactions between clays and organic pollutants Proc. Inter. Clay Conf., Mexico City, 1975 Wilmette, Illinois Applied Publishing 469475.Google Scholar
White, J. L., Kaufman, D. D., Still, G. G., Paulson, G. D. and Bandai, S. K., 1976 Clay-pesticide interactions Bound and Conjugated Pesticide Residues Washington, D.C. Amer. Chem. Soc 208218.CrossRefGoogle Scholar
Wilmshurt, J. K. and Bernstein, H. J., 1957 The vibrational spectra of pyridine, pyridine-4-d, pyridine-2,6-d2 and pyridine-3,5-d2 Can. J. Chem. 35 11831194.CrossRefGoogle Scholar