LDiaz-Torres Mex-Kor 2014 UANL

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    Photoluminescent andPhotocatalytic Properties of TiO2

    decorated Bismuth doped

    Strontium AluminatesL.A. Daz-Torres1

    Carlos R. Garca1, P. Salas2, M. Guzmn1

    1.Centro de Investigaciones en ptica A. C. Len Mxico2. Centro de Fsica Aplicada y Tecnologa Avanzada. Universidad

    Nacional Autnoma de Mxico.June 2014

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    Introduction

    Funct ional

    materials

    OpticalMagnetic

    Electrical

    Catalytic

    Chemical

    Luminescence

    Photocatalysis

    Multifunctional

    TiO2 decorated Bi

    doped Strontium

    aluminates

    Phosphorescent materials (PMs)Emergency signaling.Compact fluorescet lamps.

    Lasting for hours. 1

    1) Materials 2010, 3, 2536-2566.

    TiO2is one of the best photocatalyst.

    SrAl2O4:Eu2+,Dy3+and Sr4Al14O25:Eu

    2+,Dy3+

    show long persistence time.

    PMs improve the photocatalyc of the TiO2

    in composites.2

    Bismuth enhance the photocatalytic

    activity of some crystalline lattices.3

    2) J. Mater Chem A, (2013), 1, 1123-1126.

    3) M Sc. and Eng. B (2011) 176, 13821387.

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    Introduction

    Sr4Al14O25: Eu,Dy can be used without irradiation to assist the Ag3PO4photocatalyst

    in water solutions. 6

    Persistent materials (PMs) create free carriers (electron or holes) which promote the

    photocatalytic process.

    Persistent materials have been proposed to help, with exciting light, the

    photocatalyst to degrade some contaminants from water and environment.5

    5) J. Mater Chem A, (2013), 1, 1123-1126.

    6) J. Mol. Cat. A, (2012), 363-364, 129-133.

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    Produ ce a decorated TiO2Bi-dop ed stront ium aluminate with a goo d

    photo catalyt ic act iv i ty under UV irradiat ion (365 nm ).

    That the deco rated TiO2 Bi-dop ed stront ium alum inate could degrade

    methylene blue (MB) dye in water solut io ns .

    That the Persistence of the stront ium alum inates im proves w ith Bism uth

    concentrat ion.

    Is it possible to ?

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    MotivationDyes in wastewater are the major pollutants.7

    Wastewater from

    textile industry.

    MB as pollutant in

    water.

    Methylene blue (MB)

    contamination dye in a

    lake.

    7) Int. J. of Env. Sci. (2012),3,3, 940-955.

    Object ives:

    1 ) Syn thes ize Eu,Dy-s t ron t ium a luminate codoped wi th d i fferen t Bi mola r concent ra tions

    betw een 0.0% and 15.0% mo l.

    2) Then deco rate i t w i th TiO2at low tem perature.

    2) Study the structura l , morp holog ica l and opt ica l proper t ies.

    3) Evaluate the pho tocatalyt ic activ i ty of the TiO2decorated samples

    in methylene blue degradat ion in so lut ions u nder UV (365 nm) irradiat ion.

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    SynthesisWe use the combustion synthesismethod with urea as fuel.

    1 2 3 4

    Stage 1

    Stage 2

    1. Dissolved nitrates

    in 15 ml of deionised

    water.

    2. Introduce the beaker

    at 600C into the preheated

    mufle.

    3. Combustion ocurred

    lasting 20-30 sec.

    4. Green phosphorescent

    foaming is obtained.

    Sr(NO3)2 ,Al(NO3)3Eu(NO3)3 Dy (NO3)3Bi(NO3)3 .

    Powders are pressed

    with 2.5 t and disks of

    1.0 g are produced.

    The disks are annealed

    at 1150C for 6h in a carbon

    reducing atmosphere

    56

    (TiO2-SrAlO-Bi)Stage 3

    Grind the disks for

    Characterization of obtained

    powders

    7

    SrAlO-Bi

    Wet mixing in ethanol

    1:1 in weight Mixture

    TiO2 : SrAlO-Bi

    Dry for 24 h and anneal

    at 450C for 1h.

    Grind and use

    as a photocatalyst.

    8

    9 10

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    Photocatalysis

    At the beginning After 190 min

    1) 0.5 mM solutions of methylene blue and 30 mg ofTiO2-SrAlO-Bi photocatalyst in water strongly

    stirred for 1 h in darkness.

    2) Then, the UV lamps (365 nm) are turned ON

    keeping the stirring. Samples of 0.2 ml are extracted

    in regular periods. Samples are centrifuged at 5000 rpm.

    3) We measure the absorbance spectrum at regular periods.

    Procedure

    UV lamps

    (365 nm)

    Quartz beakerfilled with the solution

    magnetic

    stirrer plate

    Reactor design

    Agilent UV-Vis cary 60 spectro photometer

    Uti l ised to measure the absorb ance spectra

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    Results

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    20 30 40 50 60 70

    SrAl2O

    4JCPDS 34-0379

    15.0%

    10.0%

    5.0%

    2.0%

    1.0%

    2tetha ()

    0.0%

    Bi, mol.%

    Structural analysis by X-ray difraction

    of the SrAlO-Bi powders.

    For low conc entra tions o f Bi

    (x= 0.0%, 1.0%, 2.0% and

    5.0 %) the pow ders are

    composed

    Mainly of the phases: SrAl2O4

    and

    Sr4Al14O25.

    For high concentrat ions of Bi

    ( x = 10.0 % and 15.0%) the

    same stront ium alum inates

    phases appear but Bi2O3phase

    also appear in theXRD patterns.

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    Morphology of the SrA lO-B i powders

    0%

    2.0%5.0%

    10% 15%

    1.0%Micrograins of irregular shapes

    are observe for all samples afterthe annealed in carbon reduced

    atmosphere.

    The sample without Bi codoping

    show particles with

    larger sizes than the othersamples.

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    400 450 500 550 600 650

    PL

    (a.u.)

    Wavelength (nm)

    0.0%

    1.0%

    2.0%

    5.0%

    7.0%

    10.0%15.0%

    = 380nmexc510 nm

    463 nm

    Bi mol.%

    0.0 2.5 5.0 7.5 10.0 12.5 15.0

    PL

    Intensity(a.u.)

    Bi concentration, mol.%

    510 nm band:SrAl2O4:Eu,Dy

    0.0 2.5 5.0 7.5 10.0 12.5 15.0

    PL

    Intensity(a.u.)

    Bi concentration, mol.%

    463 nm band: Sr4Al

    14O

    25:Eu,Dy

    Photo lum inescence of the SrA lO-B i

    powders.

    The samp le codop ing w ith the 1.0 % of Bi

    show the h ighest luminescence when is

    exci ted with 380 nm UV l ight .

    As B i concentrat ion increases the

    lum inescence intensi ty decreases and

    a shi f t to the blue region is ob served.

    Tendenc ies of the 510 nm and 463 nm

    lumin escence bands as a funct ion of B i

    codoping.

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    For photocatalysis we select the 0%, 2.0 %, 15.0%and pure TiO2 in order to

    evaluate the methylene blue degradation.

    These samples were decorated with TiO2 and then the photocatalysis experimentwas made for each sample.

    TiO2- decorated SrAlO-B i fo r pho tocatalysis

    20 30 40 50 60 70

    0

    50

    100

    150

    200

    250

    300

    350

    counts

    2 )

    TiO2Anatase phase JCPDS 84-1286

    20 30 40 50 60 700

    20

    40

    60

    80

    100

    120

    140

    **

    *

    * *

    ***

    *

    **

    **

    **

    counts

    2

    strontium aluminates phasesTiO

    2anatase phase

    *

    XRD pattern of the 2.0 % sample after decorated with TiO2

    Pure commercial TiO2 Decorated TiO2-SrAlO-Bi-2.0 %

    powder sample

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    TiO2- decorated SrAlO-B i fo r pho tocatalysis

    Morphology of the pure TiO2and the TiO2-decorated SrAlO-Bi 2.0%

    Pure TiO2 TiO2- decorated SrA lO Bi 2.0%

    Aparent ly the TiO2nanop art ic les are attached to th e surface of the

    large micro grains o f the SrAlO-Bi 2.0 % samp le.

    This fact is benef icial for the photo catalyt ic act iv i ty because the su rface

    area is enhanc e.

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    0 50 100 150 2000

    25

    50

    75

    100

    %D

    egradation

    Exposure time (min)

    0.0% Bi

    2.0% Bi15.0% Bi

    Reference Only TiO2

    Photocatalyt ic degradat ion of of methylene blue

    under UV (365 nm ) ligh t.

    The 2.0 % B i TiO2decorated SrAlO sample reach almost a complete

    degradat ion after 210 m in o f UV irradiation .

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    ConclusionsLong persistent green and grenish blue materials were produced bythe combustion synthesis method followed by annealing in a reducingcarbon atmosphere.

    The persistent powders were decorated with TiO2and the photocatalyticactivity was evaluated for the concentrations of x= 0.0%, 2.0%, 15.0%and pure TiO

    2.

    The decorated TiO2SrAlO 2.0 % Bi-codoping sample show goodphotocatalytic activity, the degradation was 97 % after 210 min underUV (365 nm) irradiation.

    The 2.0 % sample show the long lasting persistence time and thePhotocatalytic activity probably due to the Bi levels into the strontiumaluminates lattices which creates electron or holes traps.