亚硫酸钠活化高锰酸钾超快速降解活性蓝4的动力学研究

活性染料的广泛应用导致大量染料废水的产生,因此染料废水的降解处理对于环境保护至关重要。探究了高锰酸钾/亚硫酸钠体系原位产生的高活性三价锰降解染料活性蓝4的动力学特性。研究发现:高锰酸钾/亚硫酸钠体系可在毫秒级时间尺度内降解活性蓝4,该体系的最佳适用pH范围是酸性至中性;亚硫酸钠和高锰酸钾浓度对于实际应用中高锰酸钾/亚硫酸钠体系经济、高效降解污染物非常重要;在pH为4.5~8.0时,三价锰氧化活性蓝4的二级反应速率常数高于10~6mol~(-1)·s~(-1)。     

TiO2/PS/Fe3O4 光催化剂的低温制备及其光催化和磁回收性能

以聚苯乙烯(PS)包覆油酸修饰过的纳米Fe3O4为磁核,在低温(90℃)、中性(pH=7左右)条件下,制备了以PS为惰性隔离层的磁载TiO2光催化剂.用X射线衍射仪(XRD)、透射电子显微镜(TEM)、傅里叶红外分光光度计(FT-IR)、振动样品磁强计(VSM)对催化剂的物相组成、形貌、表面性质、磁学性质进行了表征.以苯酚为模拟污染物,考察了其光催化活性,以自制的磁回收装置,考察其回收特性.结果表明,低温制备的TiO2为锐钛矿结构,平均粒径为2～5 nm,催化剂TiO2/PS/Fe3O4[其中物质的量比为n(TiO2)∶n(St)∶n(Fe3O4)=60∶2.5∶1]具有结构完整的壳/壳/核结构,TiO2在PS/Fe3O4表面负载牢固;光催化降解苯酚遵循一级反应动力学方程,TiO2/PS/Fe3O4[n(TiO2)∶n(St)∶n(Fe3O4)=60∶2.5∶1]的反应速率常数K=0.025 8,与纯TiO2的活性接近(K=0.026 2);循环使用5次后,反应速率常数仅降低0.003 4.所制催化剂具有较强的磁感应强度,平均回收率可达到92%以上.该低温水解法制备的磁载TiO2光催化剂具有良好的应用前景.     

细菌B1胞外活性物质对球形棕囊藻的溶藻机制初探

为探讨溶藻细菌B1对球形棕囊藻的溶藻作用机理及起作用的胞外活性物质的类别,研究了从珠海香洲码头赤潮海水中分离获得的溶藻细菌BI的无菌滤液对球形棕囊藻生长过程中的叶绿素a含量、丙二醛含量(MDA)、超氧化物歧化酶(SOD)和过氧化氢酶(CAT)活性的影响,并对溶藻细菌B1分泌的胞外活性物质进行了初步分析.当100 mL藻液中加入1 mL的无菌滤液,除藻率达到了83％.B1无菌滤液使藻中丙二醛的含量显著上升,48 h达到最大值153％,球形棕囊藻的SOD、CAT活性在处理开始后保持下降趋势,分别在96 h、48 h达到最低值27％、33％.研究表明B1无菌滤液(不大于1 mL)对棕囊藻的溶藻效果与加入的量成正比,且主要通过降低机体中保护酶的活性和加剧膜脂质过氧化的程度等来抑制球形棕囊藻的生长;细菌B1分泌的胞外活性物质中可能含有芳香醛类且包括载有磷基团的有机物,但不含蛋白质.     

太湖春季和秋季蓝藻光合作用活性研究

采用Phyto-PAM浮游植物分析仪测定太湖蓝藻光合作用活性的时空间分布.结果表明,太湖蓝藻光合活性具有显著的时空差异:春季蓝藻的最大光量子产量F_v/F_m (可变荧光和最大荧光之比)和实际光量子产量F_v'/F_m'分别在0.35~0.49和0.16~0.29之间,秋季蓝藻分别在 0.33~0.53和0.21~0.43之间,太湖秋季蓝藻的最大光合作用能力和实际光合作用能力大于春季蓝藻.春季和秋季蓝藻的非光化学淬灭NPQ(non-photochemical quenching)分别在0.012~0.17和0.035~0.26之间,秋季蓝藻的NPQ高于春季蓝藻,说明秋季蓝藻的自我保护能力高于春季蓝藻.快速光响应曲线(Rapid light curve, RLC)的特征参数表明春季蓝藻的光能利用效率、最大电子传递速率和光饱和强度点高于秋季蓝藻;从空间分布来看,蓝藻的最大光合作用能力、实际光合作用能力和光合作用效率在营养水平低和有水草分布的湖区相对较低,富营养化水平高的湖区则相对较高.因此,降低太湖营养盐浓度,恢复水生植物,能够抑制蓝藻的光合作用活性和生长,从而降低蓝藻水华强度.     

Enhanced photocatalytic activity of quantum-dot-sensitized one-dimensionally-ordered ZnO nanorod photocatalyst

An efficient photocatalyst was fabricated by assembling quantum dots （QDs） onto one-dimensionally-ordered ZnO nanorods, and the photocatalytic properties for Methyl Orange degradation were investigated by scanning electron microscopy, transmission electron microscopy, X-ray diffraction, UV-Vis-NIR absorption spectroscopy and photoluminescence. The results indicate that the catalyst with assembled QDs is more favorable for the degradation than the pristine ZnO nanorods. The QDs with core-shell structure lower the photocatalytic ability due to the higher carder transport barrier of the ZnS shell layer. Besides its degradation efficiency, the photocatalyst has several advantages given that the one-dimensionally-ordered ZnO nanorods have been grown directly on indium tin oxide substrates. The article provides a new method to design an effective and easily recyclable photocatalyst.     

Waste oyster shell as a kind of active filler to treat the combined wastewater at an estuary

Estuaries have been described as one of the most difficult environments on Earth. It is difficult to know how to treat the combined wastewater in tidal rivers at the estuary, where the situation is very different from ordinary fresh water rivers. Waste oyster shell was used as the active filler in this study in a bio-contact oxidation tank to treat the combined wastewater at the Fengtang Tidal River. With a middle-experimental scale of 360 ma/day, the average removal efficiency of COD, BOD, NH3-N, TP and TSS was 80.05%, 85.02%, 86.59%, 50.58% and 85.32%, respectively, in this bio-contact oxidation process. The living microbes in the biofilms on the waste oyster shell in this bio-contact oxidation tank, which were mainly composed of zoogloea, protozoa and micro-metazoa species, revealed that waste oyster shell as the filler was suitable material for combined wastewater degradation. This treatment method using waste oyster shell as active filler was then applied in a mangrove demonstration area for water quality improvement near the experiment area, with a treatment volume of 5 × 10^3 m^3/day. Another project was also successfully applied in a constructed wetland, with a wastewater treatment volume of 1 ×10^3 m^3/day. This technology is therefore feasible and can easily be applied on a larger scale,     

磁性多孔陶粒生物膜反应器处理焦化废水的试验研究

以磁性材料为原料,经过特定的工艺处理,对多孔陶瓷进行磁化改性获得磁性多孔载体,并将该载体应用于生物膜反应器中进行焦化废水处理试验。对不同类型的多孔陶粒载体进行对比试验,结果表明:磁性载体生物膜反应器对COD、NH3-N的去除率比普通活性污泥法高出25%³0%,比非载体生物膜反应器高出15%30%,比非载体生物膜反应器高出15%²0%左右。反应器的曝气量为1.5 L/h,曝气时间为10 h/d,温度为2520%左右。反应器的曝气量为1.5 L/h,曝气时间为10 h/d,温度为25³0℃。焦化废水经磁性载体生物膜反应器处理后,上清液中COD,NH3-N的去除率均在90%左右。出水浓度达到国家工业废水排放二级标准(GB18918-2002)。     

活性焦烟气脱硫技术在大型燃煤电站的应用

本文通过分析活性焦烟气脱硫技术的主要原理、工艺流程、主要原料消耗、脱硫副产品综合利用、SO2污染物达标情况,探讨该技术在内蒙古地区大型燃煤电站脱硫工程应用的可行性.     

UV-Fenton体系处理活性黑KNB染料废水的实验研究

采用UV-Fenton体系处理活性黑KNB染料废水.研究了pH值、H2O2和FeSO4用量、反应温度和反应时间等对染料废水脱色率的影响.实验结果表明,当KNB的初始浓度为50mg/L时,在t=25℃、pH =5.4、[H2O2]=0.2ml/L,[FeSO4]=0.7mmol/L,使用30W的紫外灯光照射条件,反应1小时后,KNB染料废水脱色率几乎可达100％.通过比较反应前后染料废水的UV-Vis吸收光谱,初步探讨了KNB的降解机理.研究表明,UV-Fenton体系可以有效地处理活性黑KNB染料废水,为该工艺处理实际染料废水提供基础数据.