苯酚在预活化聚酰胺膜酪氨酸酶生物传感器上的响应特性

研究苯酚在预活化聚酰胺膜酪氨酸酶生物传感器上的响应特性,适量儿茶酚的存在可加快传感器到达恒态的速度。被固定酶的量、活性及传感器的有效面积等是影响检测灵敏度的主要因素。首次采用预活化聚酰胺膜固定酪氨酸酶,并与浸蜡石墨电极组合成酪氨酸酶生物传感器,在温度２５℃电位－０．２００ＶｖｓＳＣＥ,儿茶酚浓度５×１０（－７）ｍｏｌ／Ｌ,底液０．１ｍｏｌ／Ｌ磷酸盐缓冲溶液ｐＨ６．５０下,采用电流法测定苯酚及水样中的酚。酶膜的制备、替换和贮存极为方便,酶膜贮存５个月未见活性下降,有良好的重现性和线性范围２×１０（－７）－１．２５×１０（－５）ｍｏｌ／Ｌ。     

气相色谱-离子选择电极检测器测定有机氯

用氯离子选择电极作为气相色谱检测器,测定了γ-BHC、三氯甲烷和四氯化碳,其检测下限分别为2.6×10~(-?),1.8×10~(-10)和1.0×10~(-10)mol.以γ-BHC为测定物的相对标准偏差为3.4％,线性范围为2.6×10~(-10)-9.8×10~(-7)mol.     

旋转电极式电除尘器技术研究

简要阐述了旋转电极式电除尘器的原理、结构、应用及特点,并总结出其除尘效率计算公式。研究结果表明：该技术能最大限度的减少二次扬尘,显著降低电除尘器出口排放浓度,对高比电阻粉尘有很好的收尘效果。与其他除尘器比较,旋转电极式电除尘器节省场地、空间和能源,性价比高,具有较广阔的应用前景。     

电化学工艺处理有机废水的研究进展

综述了目前国内外学者在二维电极和三维电极的开发和改进方面的研究成果,指出了电化学氧化技术和电极材料的主要研究方向和发展趋势.提出为解决电化学水处理技术中提高电催化效率和延长电极寿命的问题,当前研究的主要方向应集中在阳极材料、反应器结构和处理工艺方面.     

BOD5测定方法的研究

通过对比实验，对BOD5的测定方法进行研究，探索用氧电极法测定BOD5的可能性和可行性，对其不足之处提出相应的解决措施，使之能更适用于科研、监测教学等方面的需要。     

等离子改性CNT/TiO2电极吸附去除水中苯酚的研究

利用电感耦合空气等离子体对涂覆法制备的CNT/TiO2复合电极进行射频放电改性处理.复合电极的表面形貌、润湿性及元素成分分别通过扫描电镜(SEM)、接触角测试仪、x射线光电子能谱(XPS)进行了表征.结果表明,改性后有利于苯酚吸附,电极比表面孔隙、亲水性、TiO2及含氧官能团均得以增加;循环伏安测试(CV)表明改性后电极比电容提高54%;改性后复合电极对苯酚的吸附量较改性前提高了45%.且等离子改性CNT/TiO2电极对苯酚的去除量随电压、苯酚初始浓度的增加而增加,吸附过程符合准二级动力学方程,吸附等温线符合Langmuir等温吸附模型.     

二维与三维电解法处理含铜废水的试验研究

以含铜废水为处理对象,考察了二维电解法的电解电压、电解时间、pH值、极间距对铜去除率的影响。在此基础上为提高处理效率,两极间填充活性炭和玻璃珠形成三维电解,确定了三维电解的最佳运行条件是极间距4cm,pH值3～4,电解电压22 V,电解135min,铜离子的去除率为80.6%。     

An antibiotic composite electrode for improving the sensitivity of electrochemically active biofilm biosensor

• Antibiotic azithromycin employed in graphite electrode for EAB biosensor. • Azithromycin at 0.5% dosage increased the sensitivity for toxic formaldehyde. • Azithromycin increased the relative abundance of Geobacter. • Azithromycin regulated thickness of electroactive biofilm. Extensive research has been carried out for improved sensitivity of electroactive biofilm-based sensor (EAB-sensor), which is recognized as a useful tool in water quality early-warning. Antibiotic that is employed widely to treat infection has been proved feasible in this study to regulate the EAB and to increase the EAB-biosensor’s sensitivity. A novel composite electrode was prepared using azithromycin (AZM) and graphite powder (GP), namely AZM@GP electrode, and was employed as the anode in EAB-biosensor. Different dosages of AZM, i.e., 2 mg, 4 mg, and 8 mg, referred to as 0.25%, 0.5% and 1% AZM@GP were under examination. Results showed that EAB-biosensor was greatly benefited from appropriate dosage of AZM (0.5% AZM@GP) with reduced start-up time period, comparatively higher voltage output, more readable electrical signal and increased inhibition rate (30%-65% higher than control sensor with GP electrode) when exposing to toxic formaldehyde. This may be attributed to the fact that AZM inhibited the growth of non-EAM without much influence on the physiologic or metabolism activities of EAM under proper dosage. Further investigation of the biofilm morphology and microbial community analysis suggested that the biofilm formation was optimized with reduced thickness and enriched Geobacter with 0.5% AZM@GP dosage. This novel electrode is easily fabricated and equipped, and therefore would be a promising way to facilitate the practical application of EAB-sensors.     

异养-电极-生物膜联合反应器脱除地下水中硝酸盐的研究

提出了异养 电极 生物膜联合反应器脱除地下水中硝酸盐的工艺 ,该反应器以异养反硝化为主 ,通过电化学段脱除异养段后水中残留的甲醇或硝酸盐、亚硝酸盐氮 .进水中碳氮比 (质量比 )从 2 2— 2 9,都可保证出水中既无亚硝酸盐积累现象 ,也无残留的甲醇 ,但甲醇略为过量时可提高反应器的处理能力 .2 4℃时处理硝酸盐氮浓度 40mg L的进水 ,反应器最大脱硝负荷为 47g (m3 ·h) .     

Enzyme-electrolytic degradation of dichloromethane: Efficiency, kinetics and mechanism

Enzymatic electrolysis cell(EEC) has advantages over microbial electrolysis cell(MEC) due to the needless of microbe inoculation and high-efficiency of enzymatic reaction. In this study, an EEC was first applied to achieve the effective degradation of halogenated organic pollutants and dichloromethane(CH_2Cl_2) was utilized as a model pollutant. The results indicate that the degradation efficiency of CH_2Cl_2 after 2 hr reaction in the EEC was almost100%, which was significantly higher than that with enzyme(51.1%) or current(19.0%). The current induced the continuous regeneration of reduced glutathione(GSH), thus CH_2Cl_2 was degraded under the catalysis of GSH-dependent dehalogenase through stepwise dechlorination, and successively formed monochloromethane(CH_3Cl) and methane(CH_4). The kinetic result shows that with a current of 15 mA, the maximum specific degradation rate of CH_2Cl_2(3.77 × 10~(-3) hr~(-1)) was increased by 5.7 times. The optimum condition for CH_2Cl_2 dechlorination was also obtained with pH, current and temperature of 7.0, 15 mA and 35°C,respectively. Importantly, this study helps to understand the behavior of enzymes and the fate of halogenated organic pollutants with EEC, providing a possible treatment technology for halogenated organic pollutants.