| Based on the large specific surface area of nanomaterials and magnetic materials recycled to avoid secondary pollution characteristics,we obtained nano magnetic materials of Fe3O4-organic compounds by using the precipitation method for the preparation of Fe3O4 magnetic nano particles and modifying nano magnetic Fe3O4 by wool hydrolysis with alkaline solution and chitosan. Through the modification to improve the appearance of Fe3O4 nanoparticles size and internal structure, at the same time improve the Fe3O4 adsorption capacity of copper ions in water.First, a certain amount of wool fibers were dissolved at a certain concentration of sodium hydroxide and temperature.In the process of preparing nano-sized Fe3O4 with ferric chloride and ferrous chloride as source of iron and sodium hydroxide as precipitating agent,different volumes of wool hydrolysis solution were added to modify Fe3O4 nanoparticles.Single factor analysis of the amount of added volume of wool hydrolysis solution was used to optimize the strongest capacity of the copper ion adsorption corresponding the volume of wool hydrolysis solution. Secondly, the Fe3O4 powders prepared by the precipitation method were modified by silane coupling agent, and then the magnetic nano-powder by coupling was processed into the degradation of chitosan solution to be modified.Then the phase, structure, morphology and components of Fe3O4 and Fe3O4 modified by wool hydrolysis solution and chitosan were characterized by means of scanning electron microscopy, transmission electron microscopy, X-ray spectroscopy, X-ray diffraction,specific surface area, thermal gravimetric analysis and testing and a vibrating sample magnetometer was used to measure the modified and unmodified Fe3O4 magnetic energy.Finally, the adsorption capacity of Fe3O4 to the copper ion, adsorption isotherm, adsorption kinetics, adsorption thermodynamics and so on were measured by UV-visible spectrophotometer. Test results showed that:(1) After adding wool hydrolysis solution improved Fe3O4 for the capacity of the copper ion adsorption. Different volumes of wool hydrolysis solution had varying degrees of increase in Fe3O4 adsorption capacity and the test found that when added 60 m L wool hydrolysis solution, the modified Fe3O4 acheieved the strongest capacity of the copper ion adsorption and was more 40% than the unmodified Fe3O4.(2)The copper ion removal rate was 25% higher than that of unmodified Fe3O4 after modification by chitosan.(3)N and S elements were found in the internal of Fe3O4 modified by wool hydrolysis solution.(4) After modified by wool hydrolysis solution and chitosan, particle size was similar to unmodified Fe3O4 and particle size were in the nanometer level. After modification, the BET Surface Area, t-Plot Micropore Area, BJH Adsorption and Desorption average pore width were decreased.(5)The nano Fe3O4 modified by wool hydrolysis solution and chitosan on copper ion adsorption fitted the highest degree in Langmuir isothermal adsorption model and quasi second order kinetic model.(6)For Fe3O4 nanoparticles modified by wool hydrolysis solution chitosan, Gibbs free energy change was less than 0, enthalpy and entropy change was greater than zero. |