高浓度J酸废液资源化技术研究

探讨了Ｎ２５３－煤油－Ｈ２ＳＯ４－ＮａＯＨ化学萃取－反萃取体系提取浓缩Ｊ酸废母液中间体的工艺特性,试验结果表明,通过萃取工艺,Ｊ酸废液中的ＣＯＤｃｒ去除率可达９５％,萃余液ＣＯＤｃｒ在５００￣２０００ｍｇ／Ｌ之间,色度去除率可达９５％,该工艺可使废母液中的回收物浓缩５－１０倍,萃取剂可以循环使用而不改变性质,损失较少。     

表面活性剂溶液回收废白土中石蜡的界面张力行为研究

用界面张力扫描方程组法测定了石蜡的EACN值（EguivalentAlkaneCarbonNumber）并合成了C_18～22烷基苯磺酸钠及C_18～22.烷基磺酸钠两种表面活性剂。对炼油厂废白土中蜡的回收实验表明,这两种表面活性剂溶剂与石蜡的界面张力较低,与十二烷基磺酸钠配伍后,石蜡的回收率可达93％。     

草浆黑液直接碱回收技术的燃烧试验研究

探讨了草浆黑液与赤铁矿流化床燃烧反应机理和工艺参数.通过差热分析得到关联式x/x_0=1-exp(-0.012t),可用于预测草浆黑液在流化床中燃烧时碱回收的转化率.实验表明,草浆黑液碱回收转化率可高达95％以上. ’     

电解法处理废料贵铅的电极极化研究

以含金银铅废料制成贵铅为原料,利用电化学热力学和动力学理论,对贵铅电解法实现金银与铅的分离和得到纯铅的电极过程极化行为与工艺条件的关系进行了研究。从而确定了贵铅电解时的电解液组成为［ｐｂ２＋］７０ｇ／Ｌ,温度为４０℃,β－萘酚／胶联合添加剂等工艺条件．同时根据动力学的研究证明了贵铅电解的电极反应速度受扩散控制,其扩散速度常数Ｋ扩＝１．９１７×１０－３ｃｍ／ｓ。扩散层厚度为０．００５１ｃｍ,在ηｋ＝７５ｍＶ时的阴极过程活化能为１６．１０ｋＪ／ｍｏｌ,为贵铅电解工业分离回收金银铅提供了可靠的理论依据和设计参数。     

溶剂萃取法提取电镀污泥氨浸出渣中的金属资源

研究硫酸浸出Ｐ５０７－煤油－硫酸体系萃取分离铁,钠皂－Ｐ２０４－煤油－硫酸体系共萃铬、铝、反萃取分离铬、铝工艺回收电镀污染氨浸渣中的金属。通过优化实验,确定了全流程的最佳工艺参数。结果表明,铁铬渣中的金属铬、铝和铁均可以高纯度盐类形式回收,可作为化学试剂使用,回收率达９５％以上。     

絮凝剂PFCS的制备及其性能研究

利用Ｈ２ＳＯ４－ＨＣｌ混酸溶解轧钢废钢渣的溶出液作原料,制成一种新型无机高分子絮凝剂聚合氯硫酸铁。试验了它的絮凝性能,并与聚全硫酸铁的絮凝效果进行了比较。实验结果表明：ＰＦＣＳ在ｐＨ＝６－９的范围内具有良好的絮凝去浊性能;絮凝条件相同,将浊工为４２５度的黄河水样处理至５度以下,ＰＦＣＳ的投用量仅需１０ｍｇ／Ｌ,而ＰＦＳ的投用量至少需２５ｍｇ／Ｌ。     

土壤有机污染的原位修复技术

介绍了土壤气相抽提、生物通风和空气喷射等3种土壤原位修复技术的概念,简述了它们修复受污染土壤的适用范围和修复机理,并对影响3种修复方法的各种因素进行了详细论述.展望了土壤气相抽提、生物通风和空气喷射技术在我国的应用前景.     

防腐漆涂装含锌废水中锌粉的回收与利用

从水性环氧富锌涂料工业涂装废水中回收废锌粉,通过加热二甲基亚砜来溶解包覆于废锌粉表面的环氧树脂漆膜,得到回收锌粉,并将其再利用制防腐漆。在沉降时间12 h、热处理温度110 ℃、热处理时间60 min的条件下,废锌粉表面上的环氧树脂被去除,可直接以金属锌粉的形态加以回收利用,回收锌粉达到GB/T 6890—2012《锌粉》中的二级标准。使用后的溶剂经旋转蒸发后可再次使用,对锌粉的回收效果无影响。回收锌粉制备的防腐漆,其防腐蚀性能良好,可比市售锌粉。     

Development and validation of HPLC methods for analysis of chlorantraniliprole insecticide in technical and commercial formulations

Effective, selective, precise and accurate liquid chromatographic analytical methods for the analysis of a novel chlorantraniliprole insecticide in technical and formulation (coragen, 20% SC) have been optimized and validated. Eight methods were designed based on different mobile phases, temperature and two HPLC columns. The mobile phase consists of two mixtures (acetonitrile:water, 70:30 and methanol:water, 70:30) with 25 or 40ºC. HPLC analysis of chlorantraniliprole was carried out at a wavelength of 260 nm, with a flow rate of 0.8 mL/min. The calibration curves showed a good linear relationship (R² ? 0.99) in the injected quantities ranged from 0.0125 to 1.00 μg. Limit of detection (LOD) was found to be 3.94 to 14.56 ng and from 5.95 to 12.93 ng using the analytical methods I to IV by MicroPack CN-10 and V-VIII by ZORBAX Eclips Plus C18 columns, respectively, based on SDslope values. ZORBAX Eclips Plus C18 column with method VI was the best one (R² = 1.00 and RSD = 0.30), short retention time (4.936 min), high theoretical plates per column (65457.15) compared to others and LOD = 6.49 ng. The accuracy of the best method was demonstrated by recovery rates of 83.04% to 98.50% for grape samples supplemented with 5, 10 and 50 mg chlorantraniliprole/kg.     

Emission rates of chlorinated volatile organics from new and used consumer products found during vapor intrusion investigations: Impact on indoor air concentrations

Consumer products can emit chlorinated volatile organic compounds (CVOCs) that complicate vapor intrusion (VI) assessments. Assessment protocols acknowledge the need to remove these products during VI investigations, but they can be problematic to identify and locate. Predicting if the products cause detectable air concentrations is also difficult since emission rate information is limited and can vary with product use and age. In this study, the emission rates of 1,2-dichloroethane, trichloroethene, tetrachloroethene, and carbon tetrachloride from four consumer products identified as indoor sources during VI field investigations were measured under laboratory conditions using a flow through system. Emissions of PCE from an adhesive container tube ranged from 1.33 ± 1.13 μg/min (unopened) to 23.9 ± 2.93 μg/min (previously opened). The laboratory-measured emission rates were used to estimate indoor air concentrations, which were then compared to concentrations measured after the products placed were into an actual residence. The estimated and measured indoor air concentrations were generally comparable, showing that emission rate information can be used to determine the relative impact of internal CVOC sources.