With the development of modern industry, the emission of carbon dioxide andwaste water containing heavy metal ions cause serious harm to the environment andhuman health. Carbon dioxide as a greenhouse gas has become a global environmentproblem and it emission lead to the global temperature increased and the sea-level rise.Removal o f h eavy m etal i ons f rom w aste w ater i s es sential due t o t heirbio-accumulation tendency, toxicity, persistency and non-biodegradability in nature.Adsorption w as c onsidered f or t he b est w ay t o de aling w ith recovery of c arbondioxide and low concentration of copper waste water, and it was used more widely.In this paper, a series of amine-functionalized mesoporous silica were preparedvia an anionic surfactant-mediated synthesis method and applied to CO2adsorptionand deep removal of copper ions from aqueous solution. With isobutyric acid, lauricacid, p almitic a cid, N-Lauroyl-L-glutamic a cid and N-stearoyl-l-glutamic acid asstructure directing agent, γ-aminopropyltriethoxysilane as co-structure directing agentand tetraethyl orthosilicate as silica source. The force of forming the silicamicelle isthe direct electrostatic interaction between the positively charged amino groups inγ-aminopropyltriethoxysilane and the negatively charged head groups in the anionicsurfactant via t he S-N+I-mechanism, and t he a lkoxysilane s ite ofγ-aminopropyltriethoxysilane is co-condensed w ith i norganic pr ecursors (tetrathtylorthosilicate) to form silica wall. The am ine-functionalized mesoporous silica wascharacterized by Fourier transform infrared spectrometer, X-ray diffraction, nitrogenphysisorption and thermogravimetric analysis. The adsorption capacity of samples forCO2and N2was measured using static method and dynamic method. The effects ofthe type of surfactant and the content of γ-aminopropyltriethoxysilane on the structureof mesoporous silica, adsorption capacity for CO2and N2, and adsorption separationfactor of CO2/N2were studied. The saturated adsorbents were regenerated by hightemperature or vacuum, and the regenerative capacity of the adsorbents was evaluated.The C12GluA-APS-0.3sample was also used to remove of Cu2+ions from aqueoussolution, and adsorption capacity for Cu2+and adsorption rate was measured in thesolution with different concentrations. Copper adsorption process had been studiedfrom both kinetic (Pseudo-first-order kinetic and Pseudo-second-order kinetic) and equilibrium (Freundlich and Langmuir) points of view for C12GluA-APS-0.3material.The adsorption isotherms of C12GluA-APS-0.3material for CO2and N2weremeasured at323.15K, and the mixture of CO2and N2was separated by pressureswing adsorption (323.15K,0M Pa) us ing C12GluA-APS-0.3as a dsorbent. Thesimulation of pressure swing adsorption was rarely reported because of a variety ofreasons, aspen adsim software was used to simulate the adsorption process in thispaper, a nd t he a ppropriate s imulation m odel was w ell de scribed t he a dsorptionprocess. In order to further the application of simulation model, the components inLigusticum chuanxiong was separated by adsorption in supercritical carbon dioxide(SC-CO2,8.8M Pa and323.15K), and then the process was simulated using aspenadsim. In order to further used simulation model and built simulation model for liquidphase a dsorption, Ligusticum chuanxiong i s a ssumed t o be a qua si-binary s ystemmade up of s lightly a dsorbed ps eudcomponents a nd s trongly a dsorbedpseudcomponents. The adsorbent was regenerated by adding a strippant in SC-CO2,and t he s lightly adsorbed ps eudcomponents a nd s trongly ps eudcomponents (therecovery of85%) were successfully obtained in the adsorption and desorption step.The effects of the adsorption time and the flow rate of strippant on the concentrationsof t he c omponents i n t he e ffluent a nd t he r ecovery of t he p roducts were al soinvestigated. The w hole a dsorption s eparation process was s imulated with a spenadsim successfully and the amount of adsorbed components on t he adsorbents waspredicted graphically. |