Ti(IV)与铜离子共掺杂的羟基磷灰石薄膜弱紫外光杀菌研究

采用共沉淀水热合成和离子交换的方法,制备了钛与铜离子共掺杂的羟基磷灰石(Ca10(PO4)6(OH)2:HAP)(HAPTiCu),以大肠杆菌为目标物,研究了不同材料负载的多孔镍网薄膜在弱紫外光下的杀菌活性.结果表明,HAPTiCu在弱紫外光下具有高效杀菌效率,并远远高于HAPTi和P25 TiO2薄膜.这主要是铜离子的抗菌与光催化分解细菌的协同作用的结果.电子自旋共振(ESR)研究表明杀菌反应的主要活性物种是O2-.HAPTiCu薄膜释放的铜离子在光催化杀菌反应过程中,被光催化还原沉积在表面,导致了较低的铜离子溶出,从而保证了材料的稳定性.     

球衣菌吸附重金属Hg2+的理化条件及其机理研究

采用球衣菌(Sphaerotglus natans)FQ32为生物吸附剂,研究了初始离子浓度、吸附剂用量、菌龄、pH值、温度和吸附时间等理化因素对其吸附重金属Hg2 的影响,并进一步研究了吸附机理.结果表明,球衣菌在Hg2 浓度为16 mg·L-1、吸附剂用量0.4g·L-1、菌龄16h、pH 7、温度30℃、吸附时间90 rmin时的优化条件下,对Hg2 的吸附量为72.86 mg·g-1;该吸附过程是一个快速的过程,在吸附5 min时,吸附量达总吸附量的74.10%,90 min达到吸附平衡;此过程符Langmuir等温方程.等温模型、透射电镜观察和红外光谱分析显示,菌体细胞表面的活性基团与Hg2 的络合反应是球衣菌吸附Hg2 的主要机理.     

管网水有机污染物成份及二氧化氯应用的优越性

随着人们生活水平的提高管网水质问题已越来越引人们的重视,这里给出了充分利用现代检测技术分析检测出的管网饮用水中有机污染物成份及其危害,并重点介绍了氯消毒过程中的消毒副产物THM的影响.以及二氧化氯替代氯气成为新一代饮用水消毒杀生剂的必然性.     

Cr3+掺杂对TiO2薄膜光催化活性的影响

采用溶胶-凝胶法制备了TiO2粉末和以釉面瓷砖为载体的TiO2薄膜,讨论了不同Cr3+掺杂浓度对TiO2光催化活性的影响,并采用UVVIS对其光学性能进行了检测.结果表明,Cr3+掺杂和釉面瓷砖的交互作用能够显著提高TiO2薄膜的光催化活性,最佳掺杂浓度为6.04×1017个·cm-3,且随着TiO2光催化活性的提高,薄膜的吸收带边发生了明显的红移,提高了可见光的利用率.     

Preparation and characterization of visible-light-active nitrogen-doped TiO2 photocatalyst

A visible-light photocatalyst was prepared by calcination of the hydrolysis product of Ti(SO4)2 with ammonia as precipitator. The color of this photocatalyst was vivid yellow. It could absorb light under 550 nm wavelength. The crystal structure of anatase was characterized by XRD. The structure analysis result of X-ray fluorescence(XRF) shows that doped-nitrogen was presented in the sample. The photocatalytic activities were evaluated using methyl orange and phenol as model pollutants. The photocatalytic activities of samples were increasing gradually with calcination temperature from 400℃ to 700℃ under UV irradiation. It can be seen that the degradation of methyl orange follows zero-order kinetics. However, the calcination temperatures have no significant influence on the degradation of phenol under sunlight. The N-doped catalyst shows higher activity than the bare one under solar irradiation.     

羟基自由基杀灭压载水赤潮入侵生物试验研究

采用羟基自由基对斯式根管藻、日本星杆藻、裸甲藻和细菌进行杀灭实验，确定杀灭入侵赤潮生物的所需OH^-比值浓度为0.68mg／L。当OH^-比值浓度达到0．68mg／L时，致死多甲藻(Peri.Spp)等10种赤潮生物效率达到99.8％，致死膝沟孢子、多甲藻孢子效率达到100％。试验数据表明，强电离先进氧化OH^-是治理赤潮有效、可行的绿色新方法。     

云南省酸雨控制区二氧化硫污染现状及综合防治措施

能源结构的特点,使酸雨控制区的二氧化硫排放量高居不下,"西电东送"将进一步增加酸雨控制区的二氧化硫排放量.必须采取严格的、切实有效的综合防治措施削减二氧化硫排放量,确保"十五"期间酸雨控制区总目标的实现.     

膨胀珍珠岩负载TiO2光催化脱色性能的研究

以钛酸四丁酯为原料 ,膨胀珍珠岩为载体 ,用溶胶 -凝胶法制备可漂浮于水面的负载型TiO2 。利用该负载型TiO2 对罗丹明B(RB)进行光催化脱色实验 ,结果表明 ,浸渍 3次的负载型TiO2 光催化活性最高 ,催化剂最佳用量为 5 0 0mg/10 0mLRB ,经 5h光照 ,对 10 0mL浓度为 1mg/L和 2 .5mg/LRB脱色率分别为 76 .6 7%和 4 7.2 7% ;该催化剂使用寿命长 ,2 5h后催化剂脱色性能没有减弱 ,可重复使用 ;经 8h光照 ,染料废水脱色效果好。     

Euglena gracilis as a model for the study of Cu and Zn toxicity and accumulation in eukaryotic cells

We have observed the effect of copper and zinc on the biology of Euglena gracilis. The cells displayed different sensitivities to these metals, as the apparent LC₅₀ for Cu²⁺ was 0.22 mM, and for Zn²⁺ it was 0.88 mM. While Zn²⁺ was able to increase cell proliferation even at 0.1 mM, the minimal CuCl₂ concentration tested (0.02 mM) was sufficient to impair cell division. Higher concentrations of these metals not only inhibited cell division in a concentration-dependent manner, but also interfered with the metabolism of E. gracilis. A higher accumulation of proteins and lipids per cell was observed at the DI₅₀ concentration for metal-treated cells. These results suggest that the test concentration of both metals leads to a failure in completing cell division. Ultrastructural analysis indicated a chloroplast disorganization in copper-treated cells, as well as the presence of electron dense granules with different shapes and sizes inside vacuoles. Microanalysis of these granules indicated an accumulation of copper, thus suggesting a detoxification role played by the vacuoles. These results indicate that E. gracilis is an efficient biological model for the study of metal poisoning in eukaryotic cells. They also indicate that copper and zinc (copper being more poisonous) had an overall toxic effect on E. gracilis and that part of the effect can be ascribed to defects in the structure of chloroplast membranes.     

Two-site kinetic modeling of bacteriophages transport through columns of saturated dune sand

Breakthrough curves, on a semi-log scale, from tests in porous media with block-input of viruses, bacteria, protozoa and colloidal particles often exhibit a typical skewness: a rather slowly rising limb and a smooth transition of a declining limb to a very long tail. One-site kinetic models fail to fit the rising and declining limbs together with the tail satisfactorily. Inclusion of an equilibrium adsorption site does not seem to improve simulation results. This was encountered in the simulation of breakthrough curves from a recent field study on the removal of bacteriophages MS2 and PRD1 by passage through dune sand. In the present study, results of laboratory experiments for the study of this issue are presented. Breakthrough curves of salt and bacteriophages MS2, PRDI, and phiX174 in 1 D column experiments have been measured. One- and two-site kinetic models have been applied to fit and predict breakthrough curves from column experiments. The two-site model fitted all breakthrough curves very satisfactorily, accounting for the skewness of the rising limb as well as for the smooth transition of the declining limb to the tail of the breakthrough curve. The one-site model does not follow the curvature of the breakthrough tail, leading to an overestimation of the inactivation rate coefficient for attached viruses. Interaction with kinetic site 1 is characterized by relatively fast attachment and slow detachment, whereas attachment to and detachment from kinetic site 2 is fast. Inactivation of viruses and interaction with kinetic site 2 provide only a minor contribution to removal. Virus removal is mainly determined by the attachment to site 1. Bacteriophage phiX174 attached more than MS2 and PRD1, which can be explained by the greater electrostatic repulsion that MS2 and PRD1 experience compared to the less negatively charged phiX174.