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Arturo A. Keller, Ph.D. - Pesticide Transport and Remediation Research

Research Objectives:

Our primary objectives are to

  • determine pesticide sorption/desorption behavior onto soil particles of various sizes and physicochemical characteristics
  • enhance pesticide removal efficiency using surfactant-aided soil washing and in-situ flushing, by selecting the most appropriate surfactant for a contaminated site.

The proposed studies is conducted at batch and column scales to simulate soil washing and in-situ flushing respectively.

Separation of primary size particles

Low-energy separation procedure (gentle shaking with water with no any chemicals being used as disperants and repeated gravitational settling) is used to separate primary soil particles, i.e. clay (<2 mm), silt (2 mm-50 mm), and sand (50 mm-2 mm) size particles. To keep the change in the properties of original clay particles as small as possible, the amount of salt solution (CaCl2) added to flocculate the clay fraction is kept to a minimum. The collected clay- and silt-sized fractions are quickly frozen using liquid nitrogen and then freeze-dried to get well separated size particles.

Batch Experiments

Sorption/desorption isotherms are determined in duplicate by the batch equilibration technique. Batch experiment is an important means to study a solute sorption behavior under equilibrium. The vigor of shaking in batch systems is very important in the mass transfer of reactive solutes between sorption sites inside porous sorbents and bulk solution. The increase of the mass transfer rate of the solute results in a faster establishment of equilibrium. The supernatant is analyzed on a HPLC or on a GC/MS/MS (Varian, 2100T) for the pesticides (Atrazine, Diuron and Lindane), and on the DCA for the surfactants. All of these analytical instruments are available in our lab.

Column Experiments

Columns are carefully packed with soils to minimize potential preferential pathways. A 20 mm nylon mesh is strapped to the bottom of the column to prevent the soils from falling out of the column. C14-labelled pesticides are used to facilitate the detection of the particle-bound pesticides. Pesticide concentrations are quantified on a liquid scintillation analyzer (Beckman LS6500). Both a total pesticide and a particle-bound pesticide concentration are measured, being subsamples from the same effluent sample. The operational defined ‘solution phase’ is taken from the supernatant after centrifuging a 10ml subsamples at 4000 ×g for 30 minutes. The particle-bound pesticide concentration is then calculated as the difference of the total amount and the solution phase.

Analysis of samples

GC/MS/MS Specifications for the Varian Gas Chromatograph - Mass Spectrometer (Saturn 2100T) can be found here.

HPLC - Shimadzu: info here

Liquid Scintillation Counter - Beckman: info here

Other physicochemical characterization

DCA Analyzer

Publications & Presentations

Sorption and Desorption of Atrazine and Diuron onto Primary Soil Particles