Oxytetracycline at Environmental Interfaces Studied by Second Harmonic Generation Patrick L. Hayes and Franz M. Geiger Department of Chemistry, Northwestern.

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Oxytetracycline at Environmental Interfaces Studied by Second Harmonic Generation Patrick L. Hayes and Franz M. Geiger Department of Chemistry, Northwestern University, Evanston IL WMRC Symposium on PPCPs in the Illinois Environment -- April 25, 2008

Oxytetracycline Morantel Konek et al. J. Am. Chem. Soc. 2005, 127, Oxytetracycline (OTC) Mifflin et al. J. Phys. Chem. B 2006, 110, Hayes et al. J. Phys. Chem. C 2007, 111, 8796.

Oxytetracycline Hileman, B. “Resistance is on the Rise” Chem. Eng. News 2001, February 19, 47. Kulshrestha, P.; Giese, R. F. Aga, D.S. Environ. Sci. Technol. 2004, 38, Boxall, A. B. A. EMBO Reports 2004, 5, Simon, N. S. Environ. Sci. Technol. 2005, 39, Tetracyclines are used in humans and cattle/poultry/swine Estimated 3 million pounds of tetracyclines used annually for growth stimulation in livestock! 25-75% of tetracyclines administered to animals are excreted in the active form. Oxytetracycline (OTC)

Antibiotic Resistance in Soil Bacteria Importance of Mobility: Case I “A Sticky Antibiotic” Bacterium Soil Particle Bacterium Soil Particle Bacterium Soil Particle Localized Soil Particle Resistant Sticky Antibiotic

Importance of Mobility: Case II “A Mobile Antibiotic” Soil Particle Resistant Soil Particle Resistant Soil Particle Resistant Soil Particle Resistant Mobile Antibiotic Antibiotic Resistance in Soil Bacteria Koike et al. Appl. Envir. Microbiol. 2007, 73, 4813.

Environmental Interfaces Control Transport, Reactivity, Bioavailability Challenges: Complexity Separating Bulk from Surface Sensitivity Second Harmonic Generation Soils Water Table Surface Waters Pollutant Plume

Second Harmonic Generation (SHG) Eisenthal, K. B. Chem. Rev. 1996, 96, Shen, Y. R. “The Principles of Nonlinear Optics” John Wiley & Sons: New York, Advantages: Surface-Specific Sensitivity Allows for Real-time Monitoring of Adsorption Experiments Run Under Flow Conditions Quartz Fundamental Laser Light Second Harmonic Generation (SHG) Water “Measurable” is E SHG  N ads Aqueous UV-Vis Spectrum Fused Quartz/Water Surface Spectrum Nitrate Surface Spectrum

Mifflin, A.L.; Gerth, K.A.; Weiss, B.M. Geiger, F.M. J. Phys. Chem. A 2003, 107, Mifflin, A.L.; Gerth, K.A.; Geiger, F.M. J. Phys. Chem. A 2003, 107, Mifflin, A.L.; Musorrafiti, M.J.; Konek, C.T.; Geiger, F.M. J. Phys. Chem. B 2005, 109, Hayes et al. J. Phys. Chem. C 2007, 111, Analyte Waste I time Aqueous Phase SiO 2 I time PMT Water Teflon Flow Cell UV-Vis laser Pulsed & Tunable Laser Experimental Setup

Sutton, R.; Sposito, G. Environ. Sci. Technol. 2005, 39, Al-Abadleh et al. J. Am. Chem. Soc. 2004, 126, Gibbs-Davis, J.M.; Hayes, P.L.; Scheidt K. A.; Geiger F.M. J. Am. Chem. Soc. 2007, 129, Hayes et al. J. Phys. Chem. C 2007, 111, Common Organic Motifs Model Environmental Interfaces Fused Quartz Our Strategy: Use synthetic chemistry to: (1)Isolate and study individual functional groups. (2)Build more complex model interfaces. Increasing Complexity Organic Adlayer Pollutant Soil Particle

SHG OTC Fused Quartz/Water OTC UV-Vis OTC Spectroscopy and Adsorption/Desorption Trace at Fused Quartz/Water Interface (pH 8) Mifflin et al. J. Phys. Chem. B 2006, 110, H2OH2O H2OH2O OTC 5 x 10 –5 M

Langmuir, D. Aqueous Environmental Geochemistry; Prentice Hall, Inc: New Jersey, Hayes et al. J. Phys. Chem. C 2007, 111, Mifflin et al. J. Phys. Chem. B 2006, 110, R =1+(  /n). K d C/C o x 0 Pollutant Water K d = 0.11 mL/g Taking: (  /n) = 4 – 10 g/cm 3 R f = R f = 2, corresponds to 50% reduction in OTC mobility relative to water. Retardation Factor: OTC Isotherm & The K d Model (pH 8)

Summary of Isotherm Experiments: Mobility Mifflin et al. J. Phys. Chem. B 2006, 110, Hayes et al. J. Phys. Chem. C 2007, 111, 8796.

Predicting OTC Mobility: Surface Energy and OTC Retardation a b c d e f For Hydrogen-Bonding Surfaces, and Taking: (  /n) = g/cm 3 (f)(e)(d)(c)(b)(a) Mifflin et al. J. Phys. Chem. B 2006, 110, Hayes et al. J. Phys. Chem. C 2007, 111, (c)  = 49º, 9 mJ/m 2  = 75º, 22 mJ/m 2 (f)

Predicting OTC Mobility: Surface Energy and OTC Retardation a b c d e f For Hydrogen-Bonding Surfaces, and Taking: (  /n) = g/cm 3 (f)(e)(d)(c)(b)(a) Mifflin et al. J. Phys. Chem. B 2006, 110, Hayes et al. J. Phys. Chem. C 2007, 111, IHSS HA Aldrich HA IHSS Humic Acid: Contact Angle: 59(3) Surface Energy: 14(1) mJ/m 2 Predicted R f : 1.4(1) Aldrich Humic Acid: Contact Angle: 57(3) Surface Energy: 13(1) mJ/m 2 Predicted R f : 1.3(1)

Connections to Mobility a b c d e f OTC will tend to be less mobile in silica-rich soils that: Contain natural organic matter with a large density of benzoic acid functional groups Display high interfacial energy Mobile OTC ???

Acknowledgements Geiger Group 2006 Professor Franz M. Geiger Dr. Amanda Mifflin (OTC) Dr. Julianne Gibbs-Davis Professor Karl A. Scheidt Funding: