地下水中阴离子对球磨零价铁除砷影响

研究了不同浓度下几种阴离子（NO₃^-、SO₄^2-、H₂PO₄^-、SiO₃^2-）对球磨零价铁（BZVI）除砷规律的影响,探讨了上述阴离子对BZVI氧化As（Ⅲ）能力的影响,三价砷及五价砷的转化机制,及BZVI腐蚀产物.研究证实,不同浓度的NO₃^-和SO₄^2-对砷去除效率影响不显著,但是随着H₂PO₄^-和SiO₃^2-浓度升高,溶液中As（V）分别由25.1%上升到83.6%和下降到3.8%;通过SEM和拉曼光谱分析发现,H₂PO₄^-促进BZVI的腐蚀,导致As（Ⅲ）氧化能力增强;而铁表面形成二氧化硅聚合物或非晶固相则是SiO₃^2-降低BZVI对砷氧化和吸附能力的主要机制.     

柴油加氢装置关键换热器管束腐蚀机理研究

目的明确兰州石化柴油加氢装置某换热器管束(主要材质为15Cr Mo钢和321不锈钢)的腐蚀失效原因。方法采用高温高压釜试验和模拟铵盐结晶试验研究15Cr Mo钢和321不锈钢在服役介质中的腐蚀机理。结果 15Cr Mo钢的腐蚀失效形式表现为铵盐结晶下的快速均匀腐蚀和其他部位的点蚀;而321不锈钢的腐蚀失效形式则相反,主要表现为铵盐结晶下的点蚀。结论为避免铵盐结晶引起的腐蚀穿孔,建议提高换热器出口温度到230℃以上,将换热器出口的注水工艺改为注中和缓蚀剂,在加氢反应器出口增设脱氯罐。     

工业换热设备的能效评价意义及方法

本文从节能角度,阐述了换热器能效评价的意义;根据换热器的用途,将其分为工艺换热器和辅助换热器,以此为基础,介绍影响换热器能效的主要因素;从我国目前对换热器能效评价的现状出发,提出热力学参数法一用传递有效度方法适合目前的技术水平现状,并简要介绍了该方法的原理和应用。本文的研究,希望对我国换热器能效评级工作有所帮助。     

污垢系数对热交换器的影响

环保、冶金及建材行业余热利用中的热交换器,常因管内污垢系数上升、换热面粘附粉尘而失效.研制用于某硅铁电炉高温烟尘治理余热利用中设有脉冲喷吹自动清灰装置的热交换器,可有效解决因粉尘粘附而导致的传热系数下降,从而保证了换热器长期稳定运行.     

新型弱碱性阴离子交换树脂对Cr(Ⅵ)的吸附性能

用氯乙酰化聚苯乙烯树脂(PS-Acyl-Cl)代替传统的氯甲基化聚苯乙烯树脂(PS-CH2-Cl),通过其与二乙胺(DEA)的胺化反应得到一种新型弱碱性阴离子交换树脂(PS-Acyl-DEA)。研究了该树脂对C(rⅥ)的静态吸附性能,以期处理含铬废水及铬的富集回收提供理论和实验依据。结果表明,该树脂对C(rⅥ)的吸附量随pH的降低而增加;吸附过程在实验浓度范围内符合Langmuir和Freundlich方程,且最大吸附量达263mg/g,大于文献报道。动力学和热力学研究表明,吸附过程为液膜扩散控制,自发且放热过程。     

2,4-二硝基酚在离子交换树脂上吸附与微波脱附

研究了717强碱阴离子交换树脂对水中2,4-二硝基苯酚(2,4-DNP)的吸附解吸性能,探讨了吸附的热力学和动力学特性及其微波脱附性能。结果表明:在pH=4～11时,该树脂对2,4-DNP有较强的吸附能力。Freundlich吸附等温方程能很好地描述吸附平衡数据,吸附过程为放热、熵减的自发过程。吸附动力学符合Lagergren二级速率方程,颗粒内扩散是吸附速率的主要控制步骤,可采用HSDM模型描述。以1mol/L HNO3+C2H5OH溶液作为脱附剂,采用微波辅助脱附再生,微波辐照累计5min时,酚脱附率可达90%以上。     

离子色谱法测定降水中阴离子含量的测量不确定度评定

使用离子色谱法,论述了测定降水中F-、CL-、NO3-、SO42-测量不确定度的方法,同时指出测量中可能导致不确定度的来源。     

零价铁去除水中锑(Sb)的研究

锑(Sb)是一种新兴的全球性污染物,在我国西南Sb矿区及周边地区Sb污染严重。本文研究了零价铁(ZVI)对Sb的去除效果,研究了ZVI投加量、Sb的初始浓度、pH值及阴离子等因素的影响。结果表明,ZVI对Sb具有较好的去除效果。通过ZVI对Sb去除动力学拟合,Sb的去除符合一级动力学方程;Sb的去除效率在偏酸性条件下比较高,在pH=5时,去除率达到68.98%;在pH=7时,Sb的去除率仅有23.36%;无机阴离子均在不同程度上影响Sb的去除,特别是PO43-对ZVI去除Sb有明显的抑制作用。     

Polyphenylene sulfide based anion exchange fiber: Synthesis, characterization and adsorption of Cr(VI)

A fibrous strong base anion exchanger (QAPPS) was prepared for the first time via chloromethylation and quaternary amination reaction of polyphenylene sulfide fiber (PPS), and its physical-chemical structure and adsorption behavior for Cr(VI) were characterized by FT-IR, Energy Dispersive Spectrometry, TG-DTG, elemental analysis and batch adsorptive technique, respectively. The novel fibrous adsorbent could effectively adsorb Cr(VI) over the pH range 1-12, the maximum adsorption capacity was 166.39 mg/g at pH 3.5, and the adsorption behavior could be described well by Langmuir isotherm equation model. The adsorption kinetics was studied using pseudo first-order and pseudo second-order models, and the t_1/2 and equilibrium adsorption time were 5 and 20 min respectively when initial Cr(VI) concentration was 100 mg/L. The saturated fibers could be regenerated rapidly by a mixed solution of 0.5 mol/L NaOH and 0.5 mol/L NaCl, and the adsorption capacity was well maintained after six adsorption-desorption cycles.     

Selection of magnetic anion exchange resins for the removal of dissolved organic and inorganic matters

Four magnetic anion exchange resins (MAERs) were used as adsorbents to purify drinking water. The effect of water quality (pH, temperature, ionic strength, etc.) on the performance of MAER for the removal of dissolved organic matter (DOM) was also investigated. Among the four studied MAERs, the strong base resin named NDMP-1 with high water content and enhanced exchange capacity exhibited the highest removal rate of dissolved organic carbon (DOC) (48.9% removal rate) and UV-absorbing substances (82.4% removal rate) with a resin dose of 10 mL/L after 30 min of contact time. The MAERs could also effectively remove inorganic matter such as sulfate, nitrate and fluoride. Because of the higher specific UV absorbance (SUVA) value, the DOM in the raw water was found to be removed more effectively than that in the clarified water by NDMP resin. The temperature showed a weak influence on the removal of DOC from 6 to 26℃, while a relatively strong one at 36℃. The removal of DOM by NDMP was also affected to some extent by the pH value. Moreover, increasing the sulfate concentration in the raw water could decrease the removal rates of DOC and UV-absorbing substances.