An aerosol process for making aluminum nitride nano-powder by decompositionof single compound diethylalumimm az-ide was described. X-ray diffraction (XRD) and transmissionelectron microscopy (TEM) were used to study c...An aerosol process for making aluminum nitride nano-powder by decompositionof single compound diethylalumimm az-ide was described. X-ray diffraction (XRD) and transmissionelectron microscopy (TEM) were used to study characters of the A1N powder. It is shown that theprocess can produce spherical A1N powder with mean particle diameters ranging from 10 to 50 nm at500-800°C. The generated amorphous A1N powder is characterized by a BET (Brunauer-Emmett-Teller)surface area of 103 m2/g and is very reactive to moisture.展开更多
Herein,we use an oxidation flow reactor,Gothenburg:Potential Aerosol Mass(Go:PAM)reactor,to investigate the secondary organic aerosol(SOA)formation from wheat straw burning.Biomass burning emissions are exposed to hig...Herein,we use an oxidation flow reactor,Gothenburg:Potential Aerosol Mass(Go:PAM)reactor,to investigate the secondary organic aerosol(SOA)formation from wheat straw burning.Biomass burning emissions are exposed to high concentrations of hydroxyl radicals(OH)to simulate processes equivalent to atmospheric oxidation of 0-2.55 days.Primary volatile organic compounds(VOCs)were investigated,and particles were measured before and after the Go:PAM reactor.The influence of water content(i.e.5%and 11%)in wheat straw was also explored.Two burning stages,the flaming stage,and non-flaming stages,were identified.Primary particle emission factors(EFs)at a water content of 11%(~3.89 g/kg-fuel)are significantly higher than those at a water content of 5%(~2.26 g/kg-fuel)during the flaming stage.However,the water content showed no significant influence at the non-flaming stage.EFs of aromatics at a non-flaming stage(321.8±46.2 mg/kg-fuel)are larger than that at a flaming stage(130.9±37.1 mg/kg-fuel).The OA enhancement ratios increased with the increase in OH exposure at first and decreased with the additional increment of OH exposure.The maximum OA enhancement ratio is~12 during the non-flaming stages,which is much higher than~1.7 during the flaming stages.The mass spectrum of the primary wheat burning organic aerosols closely resembles that of resolved biomass burning organic aerosols(BBOA)based on measurements in ambient air.Our results show that large gap(0%-90%)still remains to estimate biomass burning SOA if only the oxidation of VOCs were included.展开更多
文摘An aerosol process for making aluminum nitride nano-powder by decompositionof single compound diethylalumimm az-ide was described. X-ray diffraction (XRD) and transmissionelectron microscopy (TEM) were used to study characters of the A1N powder. It is shown that theprocess can produce spherical A1N powder with mean particle diameters ranging from 10 to 50 nm at500-800°C. The generated amorphous A1N powder is characterized by a BET (Brunauer-Emmett-Teller)surface area of 103 m2/g and is very reactive to moisture.
基金supported by National Natural Science Foundation of China(Nos.51636003,91844301,41977179)Beijing Municipal Science and Technology Commission(No.Z201100008220011)+2 种基金Natural Science Foundation of Beijing(No.8192022)China Postdoctoral Science Foundation(No.2020M680242)the Open Research Fund of State Key Laboratory of Multi-phase Complex Systems(No.MPCS-2021-D-12)
文摘Herein,we use an oxidation flow reactor,Gothenburg:Potential Aerosol Mass(Go:PAM)reactor,to investigate the secondary organic aerosol(SOA)formation from wheat straw burning.Biomass burning emissions are exposed to high concentrations of hydroxyl radicals(OH)to simulate processes equivalent to atmospheric oxidation of 0-2.55 days.Primary volatile organic compounds(VOCs)were investigated,and particles were measured before and after the Go:PAM reactor.The influence of water content(i.e.5%and 11%)in wheat straw was also explored.Two burning stages,the flaming stage,and non-flaming stages,were identified.Primary particle emission factors(EFs)at a water content of 11%(~3.89 g/kg-fuel)are significantly higher than those at a water content of 5%(~2.26 g/kg-fuel)during the flaming stage.However,the water content showed no significant influence at the non-flaming stage.EFs of aromatics at a non-flaming stage(321.8±46.2 mg/kg-fuel)are larger than that at a flaming stage(130.9±37.1 mg/kg-fuel).The OA enhancement ratios increased with the increase in OH exposure at first and decreased with the additional increment of OH exposure.The maximum OA enhancement ratio is~12 during the non-flaming stages,which is much higher than~1.7 during the flaming stages.The mass spectrum of the primary wheat burning organic aerosols closely resembles that of resolved biomass burning organic aerosols(BBOA)based on measurements in ambient air.Our results show that large gap(0%-90%)still remains to estimate biomass burning SOA if only the oxidation of VOCs were included.
