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Preparation Of Carbon-based Composite And Its Application In Wastewater Purification

Posted on:2021-06-17Degree:MasterType:Thesis
Country:ChinaCandidate:H M SongFull Text:PDF
GTID:2491306029451864Subject:Materials engineering
Abstract/Summary:PDF Full Text Request
Fenton system has been widely used in the treatment of organic wastewater ousing to its advantages of strong oxidation ability(·OH)fast reaction rate and mild reaction condition.However,the traditional Fenton reaction also has several shortcomings such as a narrow suitable p H(p H=2-4),limited catalytic ability of free Fe2+ion,deactivation and reutilization difficult of external H2O2.In this paper,a novel and efficient carbon-based composite heterogeneous photocatalyst was successfully prepared based on carbon materials to construct graphitic carbon nitride/reduced graphene(g-C3N4/r GO),three-dimensional ordered macroporousα-Fe2O3/graphene aerogel(3DOMα-Fe2O3/GA)andα-Fe2O3/orange biochar(α-Fe2O3/OC)solar photo-Fenton system.Due to its excellent electron mobility,high specific surface area and carbon-based materials could enhance the light harvesting efficiency,suppress charge recombination and improve the stability of photo-reponses,which making more photo-generated electrons(e-)participate in Fenton reaction and more holes(h+)proceed the direct oxidation.At the same time,it enhanced the photo-Fenton activites towards organic pollutants,realized the photo-Fenton with self-supplied H2O2 and recycled the catalyst after the reaction.The main contents and results were as follows:1)Heterogeneous solar photo-Fenton degradation of Rh B over g-C3N4/r GO catalyst with self-synthesizing H2O2The g-C3N4/r GO catalyst was fabricated rationally by hydrothermal calcination method using melamine and r GO as raw materials.The results demonstrated that 58 mmol/L amount with self-supplied H2O2 and 87%degradation of Rh B was achieved in 120 min under the optimum conditions:p H=3.5 and loading 15%the amount of r GO.It was attributed to the fact that the g-C3N4 absorbed amounts of photons with enough energy,the photo-generated electrons in the CB of g-C3N4 transfered into the r GO,consequently improving the electron-hole separation and inhibiting self recombination of photo-generated charge carries.As the same time,the holes proceeds the direct oxidation in the VB of a g-C3N4 and the electrons on r GO were reduced by two-electron reduction of O2 to selectively produce H2O2 oxidation Fe2+for organic contaminants removal mainly triggered by the solar photo-Fenton process.2)Heterogeneous neutral solar photo-electro-Fenton degradation of Rh B over 3DOMα-Fe2O3/GA catalystThe 3DOMα-Fe2O3/GA electrode was fabricated rationally by vertical impregnation,solvent evaporation and template calcination.The results showed that 34 mmol/L amount with self-supplied H2O2 and 96.8%degradation of Rh B was achieved in 60 min under the optimum conditions:p H=7.It was attributed to the fact that the 3DOMα-Fe2O3 absorbed amounts of photons with enough energy under the action of multiple scattering and slow photo effect,the photo-generated electrons in the CB ofα-Fe2O3 transfered into the GA surface,consequently improving the electron-hole separation and inhibiting self recombination of photo-generated charge carries.As the same time,the holes proceeds the direct oxidation in the VB ofα-Fe2O3 and the electrons on GA surface were reduced by two-electron reduction of O2 to selectively produce H2O2 oxidation Fe/Fefor organic contaminants removal mainly triggered by the solar photo-electro-Fenton process.3)Heterogeneous solar photo-Fenton degradation of MO over biochar enhancedα-Fe2O3catalystTheα-Fe2O3/OC catalyst was fabricated rationally by coprecipitation-oxygen limited and temperature controlled-calcination method.The results exhibited that 97%degradation of MO was achieved in 80 min under the optimum conditions:p H=3 and the mass ratio of 1:1(C:Fe).It was attributed to the fact that theα-Fe2O3 absorbed amounts of photons with enough energy,the photo-generated electrons in the CB ofα-Fe2O3 transfered into the OC,consequently improving the electron-hole separation and inhibiting self recombination of photo-generated charge carries.As the same time,the holes proceedd the direct oxidation in the VB ofα-Fe2O3 and the electrons on OC assisted nanocrystalsα-Fe2O3 to catalyze H2O2 for organic contaminants removal mainly triggered by the solar photo-Fenton process.4)Polyethylenimine modified bamboo biochar adsorbent(PEI@BC)for highly effective adsorption of heavy metal ionsMuch more attention has been paid to biochar for improved heavy metal wastewater treatment due to large porocity,huge specific surface area and being rich in oxygen-containing functional groups.The PEI was grafted onto the BC substrate via the cross-linking reaction,which improved the adsorption capacity of BC for heavy metal pollutants.The results demonstrated that the kinetics suited the pseudo-second-order model better and the equilibrium date well fitted the Langmuir model,with adsorption capacities of 54.2,106.64 and 80.58 mg·g-1 for Cu2+,Pb2+and Cd2+within 6 h.It was attributed to the fact that the PEI grafted onto the BC provided a large number of amine groups,which could react with heavy matal ions in static electricity or complexation.As the same time,the BC increased adsorption sites with higher metal sorption capacity after PEI modification.
Keywords/Search Tags:hydroxyl radical, heterogeneous-Fenton system, reduced graphene, graphene aerogel, biochar
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