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Carbonaceous Adsorbents: Design, Fabrication and Application in Water Treatment Lunhong Ai Chemical Synthesis and Pollution Control Key Laboratory of Sichuan.

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Presentation on theme: "Carbonaceous Adsorbents: Design, Fabrication and Application in Water Treatment Lunhong Ai Chemical Synthesis and Pollution Control Key Laboratory of Sichuan."— Presentation transcript:

1 Carbonaceous Adsorbents: Design, Fabrication and Application in Water Treatment
Lunhong Ai Chemical Synthesis and Pollution Control Key Laboratory of Sichuan Province, College of Chemistry and Chemical Engineering, China West Normal University

2 Contaminated Rivers and Lakers
2

3 Water treatment methods
biological treatment coagulation/flocculation ion exchange Water Treatment membrane filtration adsorption advanced oxidation technology

4 Available adsorbents Carbonaceous materials Nanomaterials Biomass
Functional polymer Biomass Adsorbent Clay Carbonaceous materials Nanomaterials Zeolites Available adsorbents

5 Carbonaceous materials for water treatment

6 L. Ai et al. / Chemical Engineering Journal 156 (2010) 243–249
1. Fabrication of activated carbon/CoFe2O4 composites and their application in water treatment (c) XRD SEM TEM AC/CFO CFO magnetic separation texture property (d) Samples BET-surface area (m2 g-1) Total pore volume (cm3 g-1) AC 909 0.47 AC/CFO 463 0.18 L. Ai et al. / Chemical Engineering Journal 156 (2010) 243–249

7 Removal of malachite green (MG)
Effect of pH Effect of initial concentration regeneration Effect of contact time

8 2. Adsorption mechanism of methyl orange (MO) and basic fuchsin (BF) on AC/CFO
L. Ai, et. al. / Desalination 262 (2010) 134–140

9 adsorption kinetics Adsorption kinetics pseudo-first-order model pseudo-second-order model Elovich model ※ adsorption kinetics was best described by the pseudo-second-order model

10 Table 1 Kinetic parameters for adsorption of dyes on AC/CFO
adsorption kinetics Table 1 Kinetic parameters for adsorption of dyes on AC/CFO Dye Pseudo-first-order Pseudo-second-order Elovich qe,exp (mg g-1) k1 (min-1) qe,cal R2 k2 (g mg-1 min-1) a b BF 49.88 0.067 6.83 0.9816 0.022 50.53 1 2.241 41.167 0.9624 MO 47.31 0.084 7.15 0.9372 0.026 47.94 0.9999 1.886 39.979 0.9531

11 Adsorption mechanisms
intraparticle diffusion intraparticle diffusion surface adsorption surface adsorption intraparticle diffusion model ※ the adsorption process was controlled by surface adsorption (boundary-layer effect) and intraparticle diffusion.

12 adsorption mechanisms
Boyd kinetic model was generally used to determine the actual rate-controlling step involved in the dye adsorption process. Boyd model ※ boundary-layer effect mainly governed the rate-limiting process of dye adsorption on AC/CFO

13 adsorption isotherms Adsorption isotherms Langmuir and Freundlich models ※ Dye adsorption behaviors onto AC/CFO could be better represented by the Langmuir model (R2 > 0.99) ※ Monolayer adsorption capacities of MO and BF determined from the Langmuir isotherm are 95.8 and mg g−1, respectively

14 adsorption isotherms Dubinin-Radushkevich (D-R) model For D-R model, the magnitude of E(mean fren energy) is useful for estimating the type of adsorption and if this value is between 8 and 16 kJ mol−1, the adsorption proceeds by surface adsorption. In this study, the E values for MO and BF are calculated to be and kJ mol−1.

15 Adsorption capacity (mg g-1) BF AC/CFO (in this study) 101.01
Table 3. Comparison of BF and MO adsorption capacities of various adsorbents Dye Adsorbents Adsorption capacity (mg g-1) BF AC/CFO (in this study) 101.01 Bottom ash 6.39 Deoiled soya 12.03 Jalshakti® 11.7 Industrial sludges 70.4 MO 95.78 Hypercrosslinked polymeric adsorbent 70.922 Banana peels 21 Orange peels 20.5 Activated Carbon 9.49 Modified sporopollenin 5.23 NH3+-MCM-41 366.57

16 Acknowledgement Financial support from the Chemical Synthesis and Pollution Control Key Laboratory of Sichuan Province and Scientific Research Start-up Foundation of China West Normal University (07B005).

17 Merry Christmas


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