High nitrate concentrations in drinking water can lead to health problems,and managing the nitrogen cycle has been considered a major challenge by the National Academy of Engineering.Nitrate in water has been extensively studied in order to balance the nitrogen cycle Electrocatalytic nitrate reduction.Electrocatalytic reduction of nitrate converts NO3-to N2 or NH3 via electricity.Synthesis of NH3 with nitrate has important economic and social significance,because it is an important chemical raw material and carbon-free fuel.The synthesis mechanism of NH3 by NO3--N is complex,and the hydrogen evolution reaction reduces the yield and current efficiency of NH3.Transition metal oxides(such as Cu O,TiO2,etc.)have attracted much attention because of their ability to form oxygen vacancies(Ov)to improve NRR performance.However,how to enrich Ov in oxides(MOx)to provide enough H(ads)to supply NRR process and the recovery of Ov has become an urgent problem.The+4 valence metal ions in MnO2and TiO2 can be reduced to+2 and+3 valence states,so MnO2 and TiO2 can easily form Ov.In this paper,MnO2 and TiO2were modified in two ways to obtain more Ov and promote the conversion of nitrate to ammonia.In the MnO2 catalytic system,one superior dual-site NRR electrocatalyst that is composed of the Ov-enriched MnO2 nanosheets(MnO2-Ov)and Pd nanoparticles(deposited on MnO2)is constructed over the three-dimensional porous nickel foam(Pd-MnO2-Ov/Ni foam).In a continuous-flow reaction cell,this electrode delivers a NO3--N conversion rate of 642 mg N m-2 electrode h-1 and a NH3 selectivity of 87.64%at-0.85 V vs.Ag/Ag Cl when feeding 22.5 mg L-1 of NO3--N.Increasing the feeding NO3--N.concentration and flow rate can further lift the conversion rate to 1933 and1171 N m-2 electrode h-1,respectively.Impacts of the NO3--N feeding concentration,flowing rate,solution p H,Pd loading mass,the coexisting anions and dissolved organic organisms on the NRR performances of Pd-MnO2-Ov/Ni foam were also investigated.The combination of experimental characterizations and theoretical calculations reveal that the MnO2-Ov adsorbs,immobilizes,and activates the NO3-and N-intermediates,while the Pd supplies the Ov sites with sufficient adsorbed hydrogen for both the NRR and Ov refreshment.In TiO2 catalytic system,TiO2 structure was modified by doping N element.N-TiO2 catalysts with different amount of nitrogen doping were prepared by calcination of Ti N at different temperatures.Compared with pure phase TiO2,doped TiO2 has better performance of electrocatalytic reduction of nitrate,and with the reduction of nitrogen content,nitrate reduction efficiency and Faraday current efficiency both increase first and then decrease in a volcanic trend.N-TiO2 fired at 650℃has the best effect.The most removal rate of NO3-can reach 90.28%,and the selectivity of NH3 can reach86.32%.Combined with the characterization and experimental results,it is shown that the doping of N makes the N-TiO2 catalyst have two crystal phases of rutile and anatase,and the content of oxygen vacancy decreases with the decrease of nitrogen content,but the gap width increases gradually,and the electron transport capacity on the catalyst changes Therefore,N doping can regulate TiO2 crystal phase structure,oxygen vacancy content and electron transfer speed,thus significantly improving the electrocatalytic nitrate reduction performanceThis study provides two facile and effective strategies to improve the catalyst removal rate for nitrate removal.The results deepen the understanding of the NRR mechanism and provide a feasible method for improving the recovery of ammonia resources by electrocatalytic reduction of nitrate.The practical feasibility from NO3-to NH4+is of great significance for the application of electrocatalytic reduction technology in practical environmental remediation. |