纳米金修饰分子印迹聚合膜电极检测双酚A

以纳米金修饰玻碳电极为基础电极,以双酚A为模板分子,以邻氨基苯硫酚为聚合单体,采用循环伏安法电聚合制备分子印迹聚合膜,利用循环伏安和交流阻抗法研究电极的电化学特性。结果表明,双酚A在修饰电极表面的反应是一个受吸附控制的等电子、质子转移的不可逆反应。采用差分脉冲伏安法检测双酚A,线性范围为5. 0×10~(-6)mol/L～4. 0×10~(-4)mol/L,检出限为2. 3×10~(-7)mol/L。将该电极用于自来水和牛奶样品的测定,结果均为未检出,加标回收率分别为93. 5%和95. 4%,3次测定结果的RSD分别为4. 0%和5. 7%。     

汽车排气尾流中微粒分布及其变化特性的研究

根据微粒核化、凝并及凝结模型对汽车排气尾流中微粒分布的变化特性进行了分析.结果表明,微粒的核化增加了排气尾流中超细微粒的数量;微粒的凝并和凝结将改变排气尾流中的微粒分布.在核化、凝并及凝结过程同时存在时,核化对微粒分布的影响相对较小,微粒分布的变化主要受凝并和凝结的作用.在排气管出口处,微粒的核化、凝并及凝结过程比较剧烈,微粒分布变化较大;随着距排气管出口距离的增加,微粒演变逐渐减弱.研究工作可以为汽车排放控制策略的确定以及汽车微粒对人体健康影响的研究提供依据.     

中小型反渗透系统处理高硬度水操作参数的优化

中小规模反渗透(RO)系统处理高硬度水时往往采用投加阻垢剂、降低回收率来减少碳酸钙在膜上结垢的风险,该系统操作参数主要是阻垢剂投加量和系统回收率。目前许多反渗透系统是凭借经验或生产厂家的建议来确定这2个参数,缺少科学、快速的求解方法。就这2个参数的确定提出了便捷办法。     

成都双流机场低能见度发生规律初探

双流机场全年近1／3的日子有低见度天气出现,最多的冬季平均日数达到的总数的80％,而且低能见度有明显的季节变化和日变化。低能见度主要由辐射雾造成。二次低能见度天气为其特点,主是由弱冷空气进入暖湿气团所致。     

Fenton氧化/混凝沉淀协同处理腈纶聚合废水

采用Fenton法处理湿法腈纶聚合废水,考察了H2O2投加量、Fe2+投加量、p H和反应时间等因素对氧化和混凝作用去除废水污染物的影响,并分析了废水可生化性和特征污染物的变化。结果表明,Fenton法可以有效去除废水中有机污染物,在初始p H为3.0,Fe2+投加量为15.0 mmol/L,H2O2投加量为90.0 mmol/L的条件下,反应120 min后废水COD去除率可以达到56.8%,其中氧化和混凝作用对应的去除率分别为43.3%和13.5%;处理后废水的BOD5/COD由0.24升高至0.43;处理后废水中丙烯腈以及其他多数有机污染物能被有效去除。     

纳米腐植酸基复合树脂的制备及其对Ni~(2+)和Cd~(2+)的吸附

采用水溶液聚合法,以丙烯酸、丙烯酰胺及改性蒙脱土为原料,纳米腐植酸为基体,N,N’-亚甲基双丙烯酰胺为交联剂,过二硫酸钾为引发剂,制备了丙烯酸-蒙脱土-丙烯酰胺/纳米腐植酸复合树脂(简称复合树脂)。考察了溶液pH、吸附时间、吸附温度、初始离子浓度等因素对复合树脂分别吸附Ni~(2+)和Cd~(2+)的影响。实验结果表明:在吸附温度35℃、吸附时间90 min、溶液pH为7、初始Ni~(2+)和Cd~(2+)的浓度分别为0.02 mol/L、复合树脂加入量16.7 g/L的条件下,Ni~(2+)和Cd~(2+)的吸附量分别为383.02 mg/g和359.27 mg/g;复合树脂吸附Ni~(2+)和Cd~(2+)的吸附等温线均满足Langmuir等温吸附方程;吸附过程均符合准二级动力学方程;复合树脂重复使用6次,其对Ni~(2+)和Cd~(2+)的吸附量分别降低了17.1%和9.3%。     

活性炭吸附回收挥发性有机物的研究进展

活性炭吸附法是目前使用范围最为广范、技术最为成熟的回收挥发性有机物（VOCs）的方法。该法与冷凝法联用,可达到经济、高效回收VOCs的目的。介绍了变压吸附和变温吸附等常见的活性炭吸附回收VOCs的工艺,分析比较了各工艺的特点,并指出了存在的问题。在总结现有研究进展的基础上,预测了活性炭吸附回收VOCs技术的发展趋势。     

ASTM D 5894-05《涂漆金属盐雾／紫外线循环暴露标准规程，（交替暴露于喷雾／干燥室和紫外线／冷凝室）》标准解读

介绍了ASTM D 5894—05,分别从标准的适用范围及用途、试验设备、试验样品、试验程序、暴露持续时间和报告等方面对标准进行解读,认为今后的盐雾试验发展方向应向人工试验和自然环境相关性方向发展。     

Experimental and modeling study of de novo formation of PCDD/PCDF on MSW fly ash

The effect of sulfur dioxide （SO2） on the formation of polychlorinated dibenzo-p-dioxins （PCDDs） and polychlorinated dibenzofurans （PCDFs） has been studied in an entrained-flow reactor （EFR） under simulated waste combustion conditions. A chlorination model based on conditional probability was employed to evaluate the homologue patterns of PCDDs and PCDFs. Results revealed that the presence of SO2 did not alter the formation pathway although SO2 suppressed PCDD/F formation. The prediction model of PCDF showed good agreement with the experimental data （R--0.95）, whereas the prediction for PCDDs did not correlate well with the experimental data. This may be explained because potential chlorination pathways play a significant role in PCDF formation, whereas PCDDs are mainly formed through condensation reactions. Furthermore, the result indicated that the steric hindrance during formation has more effects on PCDD than on PCDF due to the symmetric molecular structures of PCDDs.     

Reaction mode between Si and Fe and evaluation of optimal species in poly-silicic-ferric coagulant

A kind of Fe-polysilicate polymer, poly-silicic-ferric （PSF） coagulant was prepared by co-polymerization （hydroxylation of mixture of Fe^3＋ and fresh polysilicic acid （PS））, in which PSF0.5, PSF1 or PSF3 denotes Si/Fe molar ratio of 0.5, 1 or 3, respectively. The effects of Si/Fe ratio and reaction time （co-polymerization time or aging time） on the reaction mode between Si and Fe were studies, and the optimal species of PSF was evaluated by pH change during the preparation of PSF and coagulation tests. The results showed that the characteristics of PSF are largely affected by both reaction time and Si/Fe ratio. PSF is found to be a essential complex of Si, Fe, and many other ions. The reaction mode between Si and Fe differs with various Si/Fe ratios. The pH of PSF0.5, PSF1 or PSF3 tended to be stable when reaction time is 10, 25 or 55 rain, respectively, which is almost consistent with the time reaching the relative stable morphology that is just the optimal species of higher coagulation efficiency. The optimal reaction time reaching optimal species can be evaluated by measuring the pH change during the polymerization process.