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One-step synthesis of nanohybrid CDs-TiO 2 composites with enhanced ultraviolet light active photocatalysis Fan Li, Feng Tian,* Changjun Liu, Zheng Wang, Zhenjie Du, Ruixin Li, Li Zhang Institute of Medical Equipment, Academy of Military Medical Sciences, Tianjin 300161, PR China TABLE S1: Crystalline characterization of different samples Sample d a (nm) FWHM CS b (nm) C-6 25.280 0.352 1.011 8.1 C-9 25.500 0.349 0.848 9.7 C-12 25.102 0.354 0.690 11.9 a Determined by XRD using the Bragg equation. b Determined by XRD using the Scherrer equation. The interplanar crystal spacing (d) and average crystallite sizes (CS) of the as-prepared C/TiO 2 samples are shown in Table 1, which were estimated using the Bragg equation () and Scherrer equation () as follows, respectively. 2sin n d cos k CS FWHM Where FWHM is the half-height width of the diffraction peak of anatase or rutile, k = 0.89 is a coefficient, θ is the diffraction angle, and λ is the X-ray wavelength corresponding to the Cu Kα radiation. Electronic Supplementary Material (ESI) for RSC Advances. This journal is © The Royal Society of Chemistry 2014

Transcript of enhanced ultraviolet light active photocatalysis One-step ...0 . 0 1 7 8 6 P e a r s o n 's r 0 . 9...

  • One-step synthesis of nanohybrid CDs-TiO2 composites with enhanced ultraviolet light active photocatalysis

    Fan Li, Feng Tian,* Changjun Liu, Zheng Wang, Zhenjie Du, Ruixin Li, Li Zhang

    Institute of Medical Equipment, Academy of Military Medical Sciences, Tianjin 300161, PR China

    TABLE S1: Crystalline characterization of different samples

    Sample 2θ da (nm) FWHM CSb (nm)

    C-6 25.280 0.352 1.011 8.1

    C-9 25.500 0.349 0.848 9.7

    C-12 25.102 0.354 0.690 11.9a Determined by XRD using the Bragg equation. b Determined by XRD using the Scherrer equation.

    The interplanar crystal spacing (d) and average crystallite sizes (CS) of the as-prepared C/TiO2 samples are shown in Table 1, which were estimated using the Bragg equation (Ⅰ) and Scherrer equation (Ⅱ) as follows, respectively.

    Ⅰ2sinnd

    Ⅱcos

    kCSFWHM

    Where FWHM is the half-height width of the diffraction peak of anatase or rutile, k = 0.89 is a coefficient, θ is the diffraction angle, and λ is the X-ray wavelength corresponding to the Cu Kα radiation.

    Electronic Supplementary Material (ESI) for RSC Advances.This journal is © The Royal Society of Chemistry 2014

  • Fig. S1 XRD pattern of the as-prepared pure CDs.

  • Fig. S2 XRD patterns of the commercial Degussa P25 and further annealed composites under different temperatures.

  • Fig. S3 SEM image of partial broken microspheres in sample C-12 (scale bar: 1 µm).

  • Fig. S4 HRTEM image of the as-prepared pure CDs (scale bar: 20 nm).

  • Fig. S5 Thermogravimetric curves of different samples from 50 ºC to 650 ºC under N2 with a same heating rate (10 ºC per min).

  • Fig. S6 FTIR spectrum of the as-prepared pure CDs.

  • Fig. S7 Fluorescent microscopy images of C-9, C-450 and pure TiO2 under the same photograph conditions.

  • Fig. S8 Photographs of P25, C-9 and C-450 that dissolved in concentrated sulfuric acid under natural light.

  • Fig. S9 Photographs of P25, C-9 and C-450 that dissolved in concentrated sulfuric acid under a UV lamp (365 nm).

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    Concentration (mg/L)

    Absorbance vs Concentration Linear Fit

    Equation y = a + b*x

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    Pearson's r 0.99711Adj. R-Squar 0.99359

    Value Standard ErrB Intercept 0.0208 0.02512B Slope 0.1672 0.00425

    Fig. S10 UV-vis absorbency of the MB solution at 664 nm with different concentrations.

  • Fig. S11 UV-vis absorbance at 664 nm monitoring the photo-degradation efficiency of CDs-TiO2 composites on MB after 10 min irradiation under UV light (254 nm).

  • Fig. S12 UV-vis absorbance at 664 nm monitoring the photo-degradation efficiency of C-TiO2 composites on MB at regular intervals under UV light (254 nm).

  • Fig. S13 UV-vis absorption spectra monitoring the degradation of MO (a, b and c) and RB (d, e and f): with C-9 as catalysts (a and d), with C-450 as catalysts (b and e) and without catalysts (c

    and f).

  • Fig. S14 Absorbance at 664 nm (MB), 554 nm (RB) and 462nm (MO) monitoring the absorption capacity of C-9 and C-450 upon the pollutants.

  • Fig. S15 UV-vis absorption spectra monitoring the degradation of MB (10 ppm) at different cycles using C-9 as the catalysts (a, b and c) and the absorbance at 664 nm monitoring the concentration

    of MB at the adsorption-desorption equilibrium of each cycle.