多晶硅切割液废液的回收与利用

结合工程实际,介绍了太阳能产业用多晶硅片切割过程中产生的割液废液的处理工艺及回收工艺,并分析了它的投资成本和经济效益。     

PVC/PES相容性及对共混超滤膜性能的影响

研究了聚氯乙烯(PVC)与聚醚砜(PES)共混体系相容性及其对共混膜性能的影响。利用溶解度参数原则和混合热焓原则进行理论预测,用铸膜液粘度法进行实验表征,均说明该体系为部分相容体系,且其相容性与组成及共混温度有关。通过对共混膜传质特性的考察,表明铸膜液的相容性会明显影响共混膜的性能;采用共混法可以改善膜性能。     

辽宁省淡水鱼类体内多溴联苯醚和六溴环十二烷的富集特征及健康风险评估

分析了辽宁省4个典型城市淡水鱼类中多溴联苯醚（PBDEs）和六溴环十二烷（HBCDs）的富集特征,并进行了健康风险评估。结果表明：淡水鱼类体内PBDEs和HBCDs检出率均为100%,PBDEs和HBCDs的平均质量分数分别为9.73 和21.81 ng/g（脂重）。PBDEs中的单体BDE 183、BDE 209和BDE 153在辽河流域不同鱼类的同源种中占优势,分别占PBDEs的26.8%～40%,17%～44%和14%～22%。在HBCDs的3种同系物中,α-HBCD是主要的单体,其相对贡献率为45.15%~84.71%。辽河流域的工厂企业生产活动对淡水鱼类产生了影响,居民通过消费水产品摄入PBDEs和HBCDs。健康风险评估结果显示：PBDEs和HBCDs的健康风险指数均＜1,说明当地水产品中PBDEs和HBCDs的非致癌风险处于可接受水平。     

间位羟基/甲氧基多溴联苯醚的合成

本文设计了3种合成路线,通过偶合反应、Baeyer-Villiger氧化水解、硝基还原、加溴反应、去甲基化等一系列反应,合成了多种间位羟基/甲基多溴联苯醚.产物经过气相色谱-质谱仪(GC-MS)和核磁共振测试表明实验所合成得到的产物与设计的目标产物结构完全一致,其纯度达到标样要求.     

β-环糊精微球吸附对苯二酚单甲基醚的动力学研究

研究了以β-环糊精(β-CD)和环氧氯丙烷为原料,采用反相悬浮聚合法合成的β-CD微球对对苯二酚单甲基醚( HQMME)的静态吸附行为,分析了吸附热力学性质和动力学特征.实验结果表明:β-CD微球对HQMME的吸附过程同时符合Lagergren一级吸附动力学方程和McKay二级吸附动力学方程;β-CD微球对HQMME的吸附等温线可同时用Langmuir等温吸附方程和Freundlich等温吸附方程描述;在不同温度下,β-CD微球吸附HQMME的吸附焓变、吸附熵变、吸附吉布斯自由能变均为负值,说明吸附是一个自发、放热的过程.     

地下水环境中甲基叔丁基醚运移过程的动力学模型

建立了地下水环境中甲基叔丁基醚(MTBE)运移过程的变系数动力学模型,并对模型进行了验证和参数灵敏度分析.模拟结果表明,地下水流速和阻滞系数对于MTBE的运移过程影响最为显著,而水动力弥散系数的影响较小,忽略其变化不会对预测地下水环境中污染物运移的环境动力学行为造成太大误差.由此得到的结论可定量研究MTBE在地下水环境中的对流.扩散特征,还可为MTBE污染地下水的预测预报、修复治理等研究提供科学依据.     

Development of inherent safety and health index for formulated product design

The numerous formulated products which are introduced to the market consist of chemical ingredients that may cause various safety and health hazards to the consumers. Therefore, it is extremely important to practice a systematic methodology to formulate products with acceptable safety and health performances. This work presents an index-based methodology to assess the safety and health hazards of the ingredients during the early formulation stage of product design. Hence, new inherent safety and health sub-indexes are introduced to improve the current safety and health hazards that are needed in formulated product design. The inherent safety and health sub-indexes are assigned with scores based on the degree of potential hazards. A higher score indicates a higher safety risk or severe health effect, and vice versa. The proposed methodology will greatly assist the users to identify the adverse safety and health effects caused by the ingredients. Hence, it is pivotal to eliminate or reduce the safety and health impacts from product usage. A case study on common ingredients used in the formulation of paint is presented on this study to describe the proposed method.     

网状聚合物冠醚对重金属离子的吸附性能

以Hg（NO3）2、Cu（NO3）2水溶液为模拟工业废水，以侧链具N、S配位基的网状聚合物冠醚为吸附剂，研究了聚合物冠醚对HP(2＋)、Cu(2＋)的吸附性能。讨论了溶液温度、pH值、金属离子浓度及时间对吸附性能的影响，该聚合物冠醚对Hg(2＋)具有较高的吸附容量和较快的吸附速度。     

空气中联苯——联苯醚的气相色谱法测定

以国产硅胶担体为固体吸附剂,采集空气中联苯-联苯醚。经热解吸、制冷、闪蒸后,用气相色谱法测定。实验结果,在常温下,国产硅胶对联苯-联苯醚的吸附率达100％;解吸回收率为97.5％:变异系数<5％;方法的检测限为0.4μg。     

Persistence of methyl <Emphasis Type="Italic">tertiary</Emphasis> butyl ether (MTBE) against metabolism by Danish vegetation

BACKGROUND: Methyl tertiary butyl ether (MTBE) is the second most highly produced industrial chemical in the US and a frequent groundwater pollutant. At the same time, MTBE is quite persistent to biotic and abiotic decomposition. The goal of this study was to find plant species that could degrade MTBE and might be used in phytoremediation. METHODS: Excised roots and leaves (0.3 g) from more than 24 Danish plant species out of 15 families were kept in glass vessels with 25 ml spiked aqueous solution for 2 to 4 days. MTBE concentrations were 1 to 5 mg/L. Samples were taken directly from the solution with a needle and injected to a purge and trap unit. MTBE and the main metabolite, TBA, were measured by GC/FID. RESULTS AND DISCUSSION: Solutions with roots of poplar (Populus robusta) and a willow hybrid (Salix viminalis x schwerinii) produced TBA in trace amounts, probably stemming from bacteria. Significant MTBE reduction (> 10%) was not observed in any of the tests. Leaves from none of the species (trees, grasses and herbs) reduced the concentration of MTBE in the solution and no TBA, nor any other known metabolite of MTBE, was detected. CONCLUSION: It was not possible to find plants capable of efficiently degrading MTBE. This gives rise to the conclusion that plants probably cannot degrade MTBE at all, or only very slowly. RECOMMENDATIONS AND OUTLOOK: For phytoremediation projects, this has, as consequence, that the volatilization by plants (except with genetically engineered plants) is the only relevant removal process for MTBE. For risk assessment of MTBE, degradation by the plant empire is not a relevant sink process.