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Adsorptive Removal of Oxytetracycline Antibiotic in Aqueous Media using Halloysite Nanoclay 1 Ecosphere Resilience Research Center, Faculty of Applied Sciences, University of Sri Jayewardenepura, Nugegoda, Sri Lanka 2 Department of Animal and Plant Sciences, The University of Sheffield, Western Bank, Sheffield, UK 3 Korea Biochar Research Center, O-Jeong Eco-Resilience Institute (OJERI) & Division of Environmental Science and Ecological Engineering, Korea University, Seoul 02841, South Korea Sammani Ramanayaka 1* , Meththika Vithanage 1 , Binoy Sarkar 2 , Yong Sik Ok 3
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  • Adsorptive Removal of Oxytetracycline Antibiotic in Aqueous Media using

    Halloysite Nanoclay

    1Ecosphere Resilience Research Center, Faculty of Applied Sciences, University of Sri Jayewardenepura,

    Nugegoda, Sri Lanka 2Department of Animal and Plant Sciences, The University of Sheffield, Western Bank, Sheffield, UK

    3Korea Biochar Research Center, O-Jeong Eco-Resilience Institute (OJERI) & Division of Environmental Science and Ecological Engineering, Korea University, Seoul 02841, South Korea

    Sammani Ramanayaka1*, Meththika Vithanage1, Binoy Sarkar2, Yong Sik Ok3

  • Introduction Emerging contaminants

    Different types of contaminants that have been detected in water bodies in trace levels Sources: • Waste water discharge • Surface runoff: Urban and Agricultural • Industrial • Ground water (e.g. landfills)

    Pharmaceuticals

    Personal care products

    Pesticides

    Industrial effluents Herbicides

    Landfill leachate

    https://www.healthcareglobal.com/top-10/top-10-innovative-pharma-companies-watch-2015 http://leachate.blogspot.com/p/what-is-leachate-landfill-leachaet.html

  • Introduction Contamination of Pharmaceuticals in Aquatic Environments

    Antibiotics are among the top pharmaceutical contaminants released from non-

    point and point sources. They are detected in elevated concentrations in ground

    and surface water as emerging contaminants due to the extensive use by humans

    and veterinary industry

  • Introduction Halloysite Nanoclay for removal of Antibiotic;

    Oxytetracycline

    • Antibiotics exhibit a poor capability of absorption (30%) in the digestive track

    • Residuals are releasing to the environment via the body excretes

    • Oxytetracycline hydrochloride (OTC) is a commonly used veterinary antibiotic,

    which is detected high levels in water

    R. Daghrir and P. Drogui, “Tetracycline antibiotics in the environment: a review,” Environ. Chem. Lett., vol. 11, no. 3, pp. 209–227, 2013.

  • Introduction Halloysite Nanoclay (HNC) for removal of Antibiotic

    • Halloysite is a naturally occurring porous nanoclay material, which can be seen in impure forms, mixed with kaolinite, montmorillonite and other clay materials

    • Porous nanoclay material consists of 10-15 bilayers of aluminosilicate rolled into a cylinder or tubular structure

    • Si and O atoms have bound together forming fused siloxane tetrahedral sheet and an edge-shared octahedral sheet, which is made up of aluminium and hydroxide

    K. Ramadass et al., “Halloysite nanotubes: Novel and eco-friendly adsorbents for high-pressure CO2 capture,” Microporous Mesoporous Mater., vol. 277, pp. 229–236, 2019.

  • Objectives Adsorptive removal of Oxytetracycline from aqueous using

    Halloysite Nanoclay

    • To assess the Oxytetracycline removal potential of HNC from aquatic environments

    under different environmental conditions i.e. pH, ionic strengths, Time and different

    initial OTC concentrations

    • To postulate mechanisms behind adsorption

    • To characterize HNC before and after oxytetracycline adsorption

  • Materials and Methodology Edge, Kinetic & Isotherm Experiments

    Edge experiment

    • Dosage of Halloysite: 1 g/L

    • Suspension was hydrated for 4 hrs

    • Nitrogen was purged in first 30 mins

    • Initial pH of the solution: 9.97

    • pH range: 3 to 9

    • Spiked OTC concentration: 25 mg/L

    • Ionic strengths: 0.1, 0.01, and 0.001 M NaNO3

  • Materials and Methodology Cont. Edge, Kinetic & Isotherm Experiments cont.

    Kinetic experiment

    • Dosage of Halloysite, and spiked OTC concentration were similar to the edge

    experiment

    • pH range: 4 to 5

    • Ionic strength: 0.001 M NaNO3

    • Time intervals of 2, 10, 20, 30, 45 min, and 1, 1.5, 2, 4, 8, 16, 24 h

  • Materials and Methodology Cont. Edge, Kinetic & Isotherm Experiments

    Isotherm experiment

    • Dosage of Halloysite: 0.5 g/L

    • Suspension was hydrated for 4h and nitrogen was purged in first 30 mins

    • Contact time: 12 h

    • pH was adjusted to 4.75

    • OTC concentration range: 10 – 500 mg/L

  • Characterization Methods

    Powder x-ray diffraction (PXRD) Rigaku Ultima IV X-Ray Powder Diffractometer with a Cu Kα radiation (λ=1.54056 nm) over a 2θ range of 3-60°

    Fourier Transformation Infrared Spectroscopy (FTIR)

    Thermo scientific NICOLET (USA) Fourier Transformation Infra-Red spectrometer in the range of 550-4000 cm-1

    Scanning Electron Microscopy (SEM) SEM images were obtained using a Field Emission Scanning Electron Microscope (FE-SEM Hitachi SU6600)

    Particle size analyzer

    UV/Vis spectrophotometer Thermo scientific GENESYS 10S Vis (USA) UV/Vis spectrophotometer in the range of 200-900 nm

    HORIBA Scientific SZ-100 particle size analyzer in the scattering angle of 90°

  • Results & Discussion Powder X-ray diffraction (PXRD)

    PXRD pattern of HNC depicts the characteristic sharp peaks at 2θ = 11.79° and 19.96° which is typical to Halloysite.

    Halloysite PXRD pattern

    PXRD pattern of Oxytetracycline hydrochloride

    2 theta (degree)

    Oxytetractcline hydrochloride PXRD pattern

  • Results & Discussion Fourier Transformation Infrared Spectroscopy (FTIR)

    Oxytetracycline chemical structure

    Oxytetracycline FTIR pattern Halloysite FTIR pattern

  • Results & Discussion Scanning Electron Microscopy (SEM)

    SEM images of Halloysite nanotubes (a) Tubular structure (magnification x100 k) and (b) Occasional aggregates of nanotubes (magnification x50 k )

  • Results & Discussion Batch Experiments - Edge

    • Oxytetracycline exists as a zwitterion in

    the range of pH 3.5–7.5

    • The point of zero charge (pHzpc) of HNC

    was determined to be pH

  • Results & Discussion Batch Experiments - Kinetics

    • A rapid adsorption was observed

    during the first 120 mins reaching

    an adsorption capacity of 17.5

    mg/g

    • The removal of OTC indicated

    reaching equilibrium after 480

    mins

    • Data modeling demonstrates the

    best fit for pseudo 2nd model

    • The kinetic data modeling of the HNC-OTC interaction illustrates both intraparticle diffusion and

    chemisorption as the mechanisms of complexation.

  • Results & Discussion Batch Experiments - Isotherm

    Hill model

    R2 0.913

    Qmax 52.38 • Data modeling demonstrates the best fit to Hill

    isotherm of OTC onto HNC

    • The maximum adsorption capacity achieved by HNC

    is 52.38 mg/g.

    • Hill model dictates a cooperative adsorption where

    multilayer adsorption takes place.

  • Results & Discussion After Adsorption

    • Oxytetracycline adsorption to HNC was confirmed with the FTIR peak analysis

    • Two main peaks of OTC can be clearly seen in the OTC adsorbed HNC

  • Results & Discussion Adsorption Mechanism

    • In low pH values, pH 2.9 to pH 3.5, a cationic form of OTC complexes with negatively charged halloysite as the pHzpc is pH 2.9 via electrostatic interaction, which is non-specific adsorption

    • Beyond pH 7.5, both OTC and halloysite become negatively charged and hence electrostatic repulsion reduces the OTC-halloysite interaction

    • Al2O3 groups (+ve) and SiO2 groups (-ve) in the inner and outer lumens of HNC allows chemisorption with the tricarbonylamide and dimethylamine in the zwitterionic form of OTC during the pH of 2.5 to 8.0 through specific adsorption

  • Conclusions

    • Oxytetracycline adsorption to the adsorbate HNC is clearly observed from FTIR results • The adsorption of Oxytetracycline is pH and ionic strength dependent and

    demonstrates high adsorption capacity at the pH of 3.5

    • OTC adsorption to HNC governs by both chemisorption and physisorption • Maximum adsorption capacity of HNC is observed as 21 mg/g

    Adsorptive Removal of Oxytetracycline Antibiotic in Aqueous Media using Halloysite NanoclayIntroduction�Emerging contaminantsIntroduction�Contamination of Pharmaceuticals in Aquatic EnvironmentsIntroduction�Halloysite Nanoclay for removal of Antibiotic; OxytetracyclineIntroduction�Halloysite Nanoclay (HNC) for removal of AntibioticObjectives�Adsorptive removal of Oxytetracycline from aqueous using Halloysite NanoclayMaterials and Methodology�Edge, Kinetic & Isotherm ExperimentsMaterials and Methodology Cont.�Edge, Kinetic & Isotherm Experiments cont.Materials and Methodology Cont.�Edge, Kinetic & Isotherm ExperimentsCharacterization Methods Results & Discussion�Powder X-ray diffraction (PXRD)��Results & Discussion�Fourier Transformation Infrared Spectroscopy (FTIR)��Results & Discussion�Scanning Electron Microscopy (SEM)��Results & Discussion�Batch Experiments - Edge��Results & Discussion�Batch Experiments - Kinetics��Results & Discussion�Batch Experiments - Isotherm��Results & Discussion�After Adsorption��Results & Discussion�Adsorption Mechanism��Conclusions


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