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Comparison of isotherm equations for boron adsorption and desorption on soils with fertilizer applications.

Giampietro Diana, Claudio Beni, Stefania Marconi

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Abstract

Adsorption and desorption of boron (B) was investigated in soils receiving different fertilizers such as mineral (21 % N), organic mineral (10% N), mycorrhizas inoculums, wine-producing residues (three different formula: distiller's residue 2.2% N; anaerobic digestate 2.8% N; the same plus mycorrhizas inoculum), and compost by farm residues (2.0% N). The soil samples, collected after a triennial lettuce (Lactuca sativa L. cv Bacio) cultivation, were equilibrated using six B concentrations (0, 1, 5, 20, 50, 100 mg B L -1 , as H 3 BO 3 ). Sorption processes were fitted to linear forms of the Freundlich, Langmuir and Temkin equations. Boron adsorption data were well described by Freundlich and Langmuir isotherms, while the Temkin showed a lowest fit. All fertilized plots showed higher intensity of adsorption (Freundlich 1/n range 0.617-0.765 L kg -1 ), and applications of distiller's residue plus anaerobic digestate and organic-mineral fertilizer to soils increased the maximum adsorption and buffering capacity, with the Langmuir and Temkin models, respectively. The Freundlich intensity of adsorption 1/n was positively correlated with the Langmuir maximum adsorption Xm and Temkin buffering capacity b. Boron desorption data fitted well with the Freundlich isotherm (high R 2 values), and the desorption intensity coefficients, 1/n 1 , increased with the application of fertilizers. Comparison of desorption to adsorption Freundlich isotherms showed that there was a total reversibility of adsorbed boron for all fertilized plots, well explained by the desorption index values <1. Freundlich isotherm proved more effective in describing B desorption in soils as compared to Langmuir and Temkin equations.

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What this paper is about

Adsorption and desorption of boron (B) was investigated in soils receiving different fertilizers such as mineral (21 % N), organic mineral (10% N), mycorrhizas inoculums, wine-producing residues (three different formula: distiller's residue 2.2% N; anaerobic digestate 2.8% N; the same plus mycorrhizas inoculum), and compost by farm residues (2.0% N). The soil samples, collected after a triennial lettuce (Lactuca sativa L. cv Bacio) cultivation, were equilibrated using six B concentrations (0, 1, 5, 20, 50, 100 mg B L -1 , as H 3 BO 3 ). Sorption processes were fitted to linear forms of the Freundlich, Langmuir and Temkin equations. Boron adsorption data were well described by Freundlich and Langmuir isotherms, while the Temkin showed a lowest fit. All fertilized plots showed higher intensity of adsorption (Freundlich 1/n range 0.617-0.765 L kg -1 ), and applications of distiller's residue plus anaerobic digestate and organic-mineral fertilizer to soils increased the maximum adsorption and buffering capacity, with the Langmuir and Temkin models, respectively. The Freundlich intensity of adsorption 1/n was positively correlated with the Langmuir maximum adsorption Xm and Temkin buffering capacity b. Boron desorption data fitted well with the Freundlich isotherm (high R 2 values), and the desorption intensity coefficients, 1/n 1 , increased with the application of fertilizers. Comparison of desorption to adsorption Freundlich isotherms showed that there was a total reversibility of adsorbed boron for all fertilized plots, well explained by the desorption index values <1. Freundlich isotherm proved more effective in describing B desorption in soils as compared to Langmuir and Temkin equations.

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Available abstract

Adsorption and desorption of boron (B) was investigated in soils receiving different fertilizers such as mineral (21 % N), organic mineral (10% N), mycorrhizas inoculums, wine-producing residues (three different formula: distiller's residue 2.2% N; anaerobic digestate 2.8% N; the same plus mycorrhizas inoculum), and compost by farm residues (2.0% N). The soil samples, collected after a triennial lettuce (Lactuca sativa L. cv Bacio) cultivation, were equilibrated using six B concentrations (0, 1, 5, 20, 50, 100 mg B L -1 , as H 3 BO 3 ). Sorption processes were fitted to linear forms of the Freundlich, Langmuir and Temkin equations. Boron adsorption data were well described by Freundlich and Langmuir isotherms, while the Temkin showed a lowest fit. All fertilized plots showed higher intensity of adsorption (Freundlich 1/n range 0.617-0.765 L kg -1 ), and applications of distiller's residue plus anaerobic digestate and organic-mineral fertilizer to soils increased the maximum adsorption and buffering capacity, with the Langmuir and Temkin models, respectively. The Freundlich intensity of adsorption 1/n was positively correlated with the Langmuir maximum adsorption Xm and Temkin buffering capacity b. Boron desorption data fitted well with the Freundlich isotherm (high R 2 values), and the desorption intensity coefficients, 1/n 1 , increased with the application of fertilizers. Comparison of desorption to adsorption Freundlich isotherms showed that there was a total reversibility of adsorbed boron for all fertilized plots, well explained by the desorption index values <1. Freundlich isotherm proved more effective in describing B desorption in soils as compared to Langmuir and Temkin equations.

Key concepts: Freundlich equation, Langmuir, Desorption, Chemistry, Adsorption, Soil water, Organic chemistry, Soil science

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