| In the paper,amorphous zero-valent iron based(G-ZVI)powders were prepared through melt-spinning method and ball-milling methods,and then the crystalline zero-valent iron based(C-ZVI)powders were prepared through ball-milling methods.The degradation efficiency and mechanism to methyl orange were evaluated.X-ray diffraction(XRD)was used to characterize and analyze the structural characteristics of zero-valent iron samples before and after degradation.Field emission scanning electron microscopy(SEM)were used to characterize the surface morphologies of the zero-valent iron sample powders before and after degradation.Energy dispersive spectrometer(EDS)was used to characterize the element types of zero-valent iron samples before and after degradation.The particle size and distribution of the obtained zero-valent iron sample powders were measured using laser particle size analyzer.X-ray photoelectron spectroscopy(XPS)was used to characterize the superficial elements,chemical valence before and after degradation.ICP-MS was used to measure the amount of iron ion after degradation.In this paper,these effects including amorphous Fe0 content,structure of Fe0,the type and content of non-metallic elements,the solution environment(pH value and temperature)and the cycling degradation efficiency of ZVI were systematically investigated.The results show that the G-ZVI powders with good dispersion and controllable particle size can be prepared by melt spinning and then ball-milling,and the average particle size of the powder can be kept at 10-30μm.The surface morphology of the powder is rugged.They have good degradation effect to methyl orange.The Fe70Si10B20G-ZVI with the lowest iron content(30 h ball milling)has the highest degradation efficiency,and the first-order degradation rate constant k=0.062 min-1,half-life t1/2=11.2min.However,Fe84Si6B10 with the highest iron content had the worst degradation efficiency,and k=0.025 min-1,half-life t1/2=27.7min,which is only 40%.Of that for Fe70Si10B20 G-ZVI.Fe75Si10B15 and Fe78Si9B13 G-ZVI have a degradation efficiency between Fe70Si10B200 and Fe84Si6B10.The ZVI powders are covered with petal-like oxidation products after degradation,which hinders the continuation of the degradation reaction.FeSiB,FeSi and FeB powders with 10-20μm particle size can be prepared through ball-milling.It was found that G-ZVIs and C-ZVIs with the same composition have a condiderable degradation efficiency.The degradation efficiency of C-ZVIs increased with the increase of B content.With the highest degradation efficiency,Fe43.64B56.36C-ZVI could degrade methyl orange by 99%in 50 min.The first-order degradation rate constant k=0.213 min-1,half-life t1/2=3.3 min.The k and t1/2 for Fe90B10 C-ZVI are0.068 min-1and 10.2 min,respectively.The k and t1/2 for Fe70B30 C-ZVI are 0.134 min-1 and 5.2 min,respectively.Si had a lower positive effect on degradation than that of B.The degradation efficiency of Fe70Si30 C-ZVI,which has k=0.046 min-1 and t1/2=15.1min,was lower than that of Fe70B30 C-ZVI.Fe43.64B56.36 C-ZVI can degrade methyl orange in acid and neutral environments.With the decrease of pH,the degradation efficiency of Fe43.64B56.36C-ZVI is improved.When the pH value was 4 and 6,the degradation half-life of methyl orange was 1 and 2 minutes,respectively.The activation energy of degradation to methyl orange for Fe43.64B56.36 C-ZVI wasΔE=19.33 kJ/mol,which was much lower than that of other zero-valent irons and confirm its excellent degradation property.The degradation efficiency of Fe70Si10B20 G-ZVI and Fe43.64B56.36 C-ZVI can maintain 90%after 20 times and 16 times cyclic utilization,respectively,which indicates that G-ZVI and C-ZVI both have a good cycling stability.There are nano-scale heterogeneity in G-ZVI.Therefor iron-rich clusters and iron-poor clusters are typical and ubiquitous,which constitute galvanic cells and promote the rapid loss of electrons in Fe0.As for the boron-containing C-ZVI,ball-milling makes the hard boron particles embedded into the soft iron particle,and can also form the iron-rich and iron-poor regions that constitute galvanic cells.Once the crystalline Fe0 begins to lose electrons,the electron loss rate of the crystalline Fe0 is comparable to that of the loosely structured amorphous Fe0,due to the defects in the crystalline state itself.Therefore,the C-ZVIs have a considerable degradation efficiency conparing to G-ZVI with the same composition.This study provides an efficient,low cost,reusable and commercial method for the degradation of azo dye wastewater. |