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Review
“Kinetics of Arsenate Adsorption –
Desorption in Solis”

Sangyul Kang
Introduction
•

There have been two major types of arsenic
in nature; As (Ⅴ) under aerobic conditions,
As (Ⅲ) under anaerobic conditions.

•

Fe and Al oxides hydroxides have a high
affinity to arsenic.

•

The objectives

1) To quantify the kinetics of adsorption and desorption of arsenate in three soils
having different physiochemical properties
2) To assess multi-reaction (equilibrium-kinetic) modeling for its capability of
describing the retention as well as the desorption or release behavior of As(V) in
different soils.
Materials and Methods
•

Materials
1)Surface soils from the Ap horizon (0-10 cm) of Olivier loam
2)Sharkey clay
3)Windsor sand

•

Method
- Batch experiments were initiated by mixing 3 g of air-dry soil with 30 mL of As(V)
solution in a 40-mL Teflon tube.
- Test were performed in triplicate.

- shake mixture at 150 rpm on a reciprocal shaker  centrifuged for 10 min at 4000
rpm after each specified reaction time.
- A 1-mL aliquot was sampled from the supernatant at reaction times of 2, 6, 12, 24,
72, 168, 336,and 504 h.
Results and Discussion
Nonlinear sorption Isotherms

•
•
•
•

Nonlinear behavior
Nonlinear or concentration – dependent adsorption behavior is
characterized by the low values of the Freundlich parameter N.
N is a measure of the extent of heterogeneity of the sorption sites having
different affinities for solute retention by matrix surfaces.
• The N values for all three soils did not vary significantly after 24 h of reaction.
• Low N values may be indicatives of extensive heterogeneity of sorption sites in
these soils.
Adsorption kinetics

• Rapid --> Gradual or slow reactions --> continued As(V) retention with
steady decrease of As(V) concentrations with reaction time
• Results concur with the nonlinear forms of the isotherms.
• These findings are in agreement with the biphasic arsenic adsorption
behavior observed on several soil minerals
Desorption Hysteresis and Binding Phases.

• Distinct discrepancies between adsorption and successive desorption
isotherms clearly indicate considerable hysteresis for As(V) release.
• This observed desorption hysteresis might be due to kinetic retention
behavior(동역학적 체류현상), such as slow diffusion (21) and irreversible
retention
Multireation Modeling

• A major implication of this study is that contamination of soils with high
concentrations of arsenic could result in slow release for extended period of
time, that is, weeks or months
• A secondary implication is that describing retention (adsorption) and
subsequent release or leaching (desorption) by use of a multiple reaction
model of the equilibrium-kinetic-irreversible nonlinear MRM type provided
good overall predictions of the fate of arsenic in the soils examined in this
study.
Thank you

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Paper reivew, kinetics of arsenate

  • 1. Review “Kinetics of Arsenate Adsorption – Desorption in Solis” Sangyul Kang
  • 2. Introduction • There have been two major types of arsenic in nature; As (Ⅴ) under aerobic conditions, As (Ⅲ) under anaerobic conditions. • Fe and Al oxides hydroxides have a high affinity to arsenic. • The objectives 1) To quantify the kinetics of adsorption and desorption of arsenate in three soils having different physiochemical properties 2) To assess multi-reaction (equilibrium-kinetic) modeling for its capability of describing the retention as well as the desorption or release behavior of As(V) in different soils.
  • 3. Materials and Methods • Materials 1)Surface soils from the Ap horizon (0-10 cm) of Olivier loam 2)Sharkey clay 3)Windsor sand • Method - Batch experiments were initiated by mixing 3 g of air-dry soil with 30 mL of As(V) solution in a 40-mL Teflon tube. - Test were performed in triplicate. - shake mixture at 150 rpm on a reciprocal shaker  centrifuged for 10 min at 4000 rpm after each specified reaction time. - A 1-mL aliquot was sampled from the supernatant at reaction times of 2, 6, 12, 24, 72, 168, 336,and 504 h.
  • 5. Nonlinear sorption Isotherms • • • • Nonlinear behavior Nonlinear or concentration – dependent adsorption behavior is characterized by the low values of the Freundlich parameter N. N is a measure of the extent of heterogeneity of the sorption sites having different affinities for solute retention by matrix surfaces. • The N values for all three soils did not vary significantly after 24 h of reaction. • Low N values may be indicatives of extensive heterogeneity of sorption sites in these soils.
  • 6. Adsorption kinetics • Rapid --> Gradual or slow reactions --> continued As(V) retention with steady decrease of As(V) concentrations with reaction time • Results concur with the nonlinear forms of the isotherms. • These findings are in agreement with the biphasic arsenic adsorption behavior observed on several soil minerals
  • 7. Desorption Hysteresis and Binding Phases. • Distinct discrepancies between adsorption and successive desorption isotherms clearly indicate considerable hysteresis for As(V) release. • This observed desorption hysteresis might be due to kinetic retention behavior(동역학적 체류현상), such as slow diffusion (21) and irreversible retention
  • 8. Multireation Modeling • A major implication of this study is that contamination of soils with high concentrations of arsenic could result in slow release for extended period of time, that is, weeks or months • A secondary implication is that describing retention (adsorption) and subsequent release or leaching (desorption) by use of a multiple reaction model of the equilibrium-kinetic-irreversible nonlinear MRM type provided good overall predictions of the fate of arsenic in the soils examined in this study.