共沉淀—原子吸收法分析铁强化盐中的铁

本文采用原子吸收分光光度法,测定铁强化盐中微量铁。用数理统计方法检证了方法的可靠性。     

用几种溶样方法对典型土样中Pb、Cr、Ni、Cd、Mn、Cu、Zn的溶出情况比较

本文采用HNO_3、HCl-HNO_3、HNO_3-H_2SO_4-HClO_4,溶洋方法消解土样,用原子吸收法测定题述中的元素,并与HCl-HNO_3-HF-HClO_4全消解方法进行了比较.发现除用HF以外的其它酸溶法Pb、Cr的溶出较少溶出比分别低于55％和67％,主要原因是Pb、Cr包藏在土壤的矿物晶格中。     

16Mn钢疲劳过程中的声发射特性研究

根据有关标准,设计加工了16Mn钢试样,并运用LOCAN320声发射仪、MTS810疲劳实验机和声发射传感器,用3种不同的试验方案,采集16Mn钢材料疲劳过程中的声发射(AcousticEmission,AE)信号特征参数,用于分析其疲劳过程中的声发射特性。重点探讨了16Mn钢材料在低周疲劳全过程中释放的声发射信号特征参数变化规律,得出声发射技术可用来评估16Mn钢材料的损伤程度,进而预测其疲劳寿命的结论。此外,充分利用试验中得到的不同疲劳载荷条件下试样的疲劳寿命,根据成组法修正了矩形截面试样16Mn钢材料的S-N曲线,经验证与实际结果吻合性较好。     

UV/Fe3+/H2O2体系降解活性艳橙X-GN废水的研究

采用UV/Fe3 /H2O2体系光解活性艳橙X-GN模拟废水,考察了X-GN,Fe3 和H2O2的初始浓度、初始pH值及温度对光解的影响,探讨了X-GN的降解途径和机理.结果表明,在8W低压汞灯(λ＝254nm)照射下,UV/Fe3 /H2O2能够有效地降解X-GN,在pH=3.0,T=50 ℃,时间为120 min,Fe3 和H2O2的初始浓度分别为2.5×10-5 mol·l-1和1.5×10-4 mol·l-1时,对含200 mg·l-1 X-GN模拟废水的色度去除率和矿化率分别达到100%和90.15%.用IC和GC/MS对X-GN降解的中间产物和最终产物进行分析,推导出UV/Fe3 /H2O2体系中X-GN降解的途径和机理.     

原子吸收光度法测定树叶中的重金属

用浓硝酸与高氯酸消解树叶,Ｃｕ、Ｚｎ、Ｍｎ含量较高,可直接用火焰原子吸收法测定,含量较低的Ｐｄ、Ｃｄ,Ｃｒ则用石墨炉法测定。Ｐｂ及Ｃｄ含量甚微,受基体及共存元素干扰严重用标准加入法可消除干扰,结果令人满意。     

Nutrient status and pollution levels in five areas around a manganese mine in southern China

• The soil TP level was high or extremely high in all areas. • TN, OM and available Cu were insufficient in EA, TA and RA. • All areas reached the heavily polluted level and had high ecological risk levels. • Mn and Cd were the dominant pollutants. Nutrient status and pollution levels are the main factors affecting soil restoration. The nutrient status and pollution levels in five areas, an unexplored mine area (UA), an explored mine area (EA), a tailings area (TA), a reclamation area (RA) and an agricultural area (AA), around the Pingle manganese mine in Guangxi, China, were assessed in this study. The results showed that the average total phosphorus in these five areas ranged from 1.05 to 1.57 mg/kg, corresponding to grades of extremely high and high. The average total nitrogen values were 0.19, 0.69, 0.93, 1.24 and 1.67 mg/kg in EA, TA, RA, UA and AA, corresponding to grades of very low, low, medium-low, medium-high and medium-high, respectively. The average organic matter values were 12.78, 8.92, 22.77, 21.29 and 29.11 mg/kg in EA, TA, RA, UA and AA, which corresponded to grades of medium-low, low, medium-high, medium-high and medium-high, respectively. All these results indicated that the total phosphorus was sufficient in these areas, while the total nitrogen and organic matter were insufficient in EA, TA and RA. The available concentrations of Mn and Zn corresponded to the intermediate grade, while the values for Cu corresponded to the very low grade; these might be another factor restricting ecological reclamation. Contamination and ecological risk assessments based on the single contamination index, Nemerow multi-factor index and potential ecological risk index showed that the five tested areas around the Mn mine were considered heavily polluted and presented high ecological risk. Mn and Cd were the dominant pollutants.     

Diphenylarsinic acid sorption mechanisms in soils using batch experiments and EXAFS spectroscopy

• DPAA sorption data was found to fit the Freundlich equation. • K_f was significantly positive correlated with oxalate-extractable Fe₂O₃. • Ligand exchange was the main mechanism for DPAA sorption on soils. • Bidentate binuclear and monodentate mononuclear DPAA bonds were identified. Diphenylarsinic acid (DPAA) is a phenyl arsenic compound derived from chemical warfare weapons. Macroscopic and microscopic work on DPAA sorption will provide useful information in predicting the partitioning and mobility of DPAA in the soil-water environment. Here, batch experiments and extended X-ray absorption fine structure (EXAFS) spectroscopy were used to investigate the sorption mechanisms of DPAA. The DPAA sorption data from 11 soil types was found to fit the Freundlich equation, and the sorption capacity, K_f, was significantly and positively correlated with oxalate-extractable Fe₂O₃. The K_f values of eight of the 11 untreated soils (1.51–113.04) significantly decreased upon removal of amorphous metal (hydr)oxides (0.51–13.37). When both amorphous and crystalline metal (hydr)oxides were removed from the untreated soils, the K_f values either decreased or slightly increased (0.65–3.09). Subsequent removal of soil organic matter from these amorphous and crystalline metal (hydr)oxide-depleted samples led to further decreases in K_f to 0.02–1.38, with only one exception (Sulfic Aquic-Orthic Halosols). These findings strongly suggest that ligand exchange reactions with amorphous metal (hydr)oxides contribute most to DPAA sorption on soils. EXAFS data provide further evidence that DPAA primarily formed bidentate binuclear (²C) and monodentate mononuclear (¹V) coring-sharing complexes with As-Fe distances of 3.34 and 3.66 Å, respectively, on Fe (hydr)oxides. Comparison of these results with earlier studies suggests that ²C and ¹V complexes of DPAA may be favored under low and high surface coverages, respectively, with the formation of ¹V bonds possibly conserving the sorption sites or decreasing the steric hindrance derived from phenyl substituents.     

Arsenic(III) and iron(II) co-oxidation by oxygen and hydrogen peroxide: Divergent reactions in the presence of organic ligands

Iron-catalyzed oxidation of As(III) to As(V) can be highly effective for toxic arsenic removal via Fenton reaction and Fe(II) oxygenation. However, the contribution of ubiquitous organic ligands is poorly understood, despite its significant role in redox chemistry of arsenic in natural and engineered systems. In this work, selected naturally occurring organic ligands and synthetic ligands in co-oxidation of Fe(II) and As(III) were examined as a function of pH, Fe(II), H₂O₂, and radical scavengers (methanol and 2-propanol) concentration. As(III) was not measurably oxidised in the presence of excess ethylenediaminetetraacetic acid (EDTA) (i.e. Fe(II):EDTA < 1:1), contrasting with the rapid oxidation of Fe(II) by O₂ and H₂O₂ at neutral pH under the same conditions. However, partial oxidation of As(III) was observed at a 2:1 ratio of Fe(II):EDTA. Rapid Fe(II) oxidation in the presence of organic ligands did not necessarily result in the coupled As(III) oxidation. Organic ligands act as both iron speciation regulators and radicals scavengers. Further quenching experiments suggested both hydroxyl radicals and high-valent Fe species contributed to As(III) oxidation. The present findings are significant for the better understanding of aquatic redox chemistry of iron and arsenic in the environment and for optimization of iron-catalyzed arsenic remediation technology.     

电感耦合等离子体发射光谱法（ICP-AES)与火焰原子吸收法（AAS）测定水中铁、锰方法对比

采用电感耦合等离子体发射光谱法、火焰原子吸收法测定水中的铁、锰,优化了测定条件。结果表明,两种方法检Ⅲ限均较低,准确度高,精密度好,具有很强的可比性。     

伊犁河水质中CODCr和CODMn的相关性探讨

对伊犁河水质中CODCr与CODMn的相关性进行了讨论。