Variations of dominant microbial populations in groundwater in response to the leachate from Laogang Landfill

Temporal changes of dominant microbial populations in groundwater in response to the leachate from Shanghai Laogang Landfill were investigated. Concentrations of dissolved redox-relevant species in groundwater suggested that the dominating redox process had changed from denitrification to methane-production/sulfate-reduction due to landfilling. Dominant microbial populations were determined using restriction fragment length polymorphism(RFLP) analyses of 16S rRNA gene libraries, which were further studied by sequencing and phylogenetic analyses. The results indicated that obvious shifts of dominant microbial populations had occurred in groundwater in response to the pollution of leachate. The closest relatives of some dominant clones are accordant with the dominating redox processes determined by hydrochemical analyses, based on the GenBank‘s indications on the ability to perform redox reactions.     

Biodegradation of azo dyes by genetically engineered azoreductase

A azoreductase gene with 537 bp was obtained by PCR amplification from Rhodobacter sphaeroides ASI. 1737. The enzyme,with a molecular weight of 18.7 kD, was efficiently expressed in Escherichia coli and its biodegradation characteristics for azo dyes were investigated. Furthermore, the reaction kinetics and mechanism of azo dyes catalyzed by the genetically engineered azoreductase were studied in detail. The presence of a hydrazo-intermediate was identified, which provided a convincing evidence for the assumption that azo dyes were degraded via an incomplete reduction stage.     

H2O浓度对强电离放电等离子体脱硫影响研究

脱除SO2过程中,H2O起着重要作用,采用强电场电离、分解H2O,生成的强氧化剂OH·将SO2直接氧化成H2SO4。就H2O浓度对强电离放电脱硫的影响进行了实验研究。结果表明,H2O浓度的越高则SO2脱除率越高;改变H2O浓度可以在不同流量下取得相同的脱硫效果;也可以根据H2O浓度来控制等离子体反应时间从而提高脱硫效果;SO2脱除率最高可达100%。     

超声波强化膜分离及清洗的研究进展

综述了超声波强化膜分离与膜清洗的机理,国内外超声波强化膜分离与清洗的研究现状以及影响该技术运用的问题所在。现有的研究成果表明:通过低功率超声波辐射处理污染膜可以减缓运行过程中的浓差极化及膜污染,而如何优化操作参数、如何减小超声波对膜体损害是近期的研究重点。     

Al13去除水中腐殖酸的混凝作用机理

研究对比了Al13、不同碱化度的聚合氯化铝(PACl)及工业聚合氯化铝等去除水中腐殖酸的絮凝特征,从Zeta电位、RT(余浊)、UV254等角度分别考察了pH值和投药量的影响,对不同形态组成絮凝剂的混凝效能有了进一步明确的认识,并且对Al13的絮凝机理进行了有益的探索．结果表明,Al13是混凝过程中的优势形态,决定着混凝剂的电中和能力．     

大气气溶胶中有机成分研究进展

有机物是大气气溶胶的重要组成部分,尤其是在细颗粒中,可占其干重的10%～70%。由于有机气溶胶的健康及气候效应,有机物的组成、源分布、颗粒行为等的研究越来越受到人们的重视。其中,有机物成分的鉴别和定量已成为近年来的研究热点。在分析中,就目前有机气溶胶的采样、有机成分提取、分离及定性、定量分析方法进行了综述,并比较了各种方法的优缺点。     

镉试剂2B固相萃取光度法测定水中微量银

研究了镉试剂2B固相萃取测定银的方法。在pH为9.5的硼砂-氢氧化钠缓冲介质中,乳化剂-OP存在下,镉试剂2B与银反应生成2∶1稳定络合物,该络合物可用pH使用范围为1~12的W atersX terraTMRP18固相萃取小柱富集,小柱上富集的络合物用乙醇(内含0.01 mol/L、pH为9.5的四氢吡咯-醋酸缓冲溶液)洗脱后用光度法测定,在洗脱剂介质中最大吸收波长为555 nm,摩尔吸光系数为1.04×105L/(mol.cm)。银质量浓度在0.01~1.0μg/mL内符合比尔定律,方法用于环境水样中银含量的测定,结果令人满意。     

低强度超声波改善污泥活性

采用城市污水处理厂的好氧活性污泥为试验材料,以好氧呼吸速率(OxygenUptakeRate,OUR)为指标,研究活性污泥在超声波强度0～1.2W/cm²、辐照时间0～40min处理后活性的变化.发现当采用超声波强度0.3W/cm²,辐照时间10min,对提高污泥活性的效果最为显著,不适当的处理时间与处理强度则不利于污泥活性的提高.因此,利用超声波激励污泥活性存在最佳的超声波强度和辐照持续时间.另外,研究了强度0.3W/cm²,辐照时间10min超声波辐射处理后0～48h中污泥活性的变化规律,发现超声辐照8h后污泥活性达到最大值,为辐射处理后初始活性的2倍,24h后超声波的强化作用基本消失.因此,可采用强度0.3W/cm²超声波每隔8h取反应器中的部分活性污泥辐照10min后再返回反应器,来提高生物反应器的处理效率.本文还对低强度的超声波改善污泥活性的可能机制进行了假说性解释.     

沙尘暴细颗粒物对大鼠肺泡巨噬细胞钙水平和脂质过氧化的影响

2004年3月采集甘肃省武威市和内蒙古包头市正常良好天气、局地扬沙天气和沙尘暴天气的大气细颗粒物(PM2．5)样品,以不同浓度的细颗粒物悬液体外处理大鼠肺泡巨噬细胞后测定细胞内丙二醛(MDA)、谷胱甘肽(IgSH)及胞质游离Ca^2 含量,并观察不同处理时间的细胞存活率．研究结果表明：(1)沙尘暴与非沙尘暴PM2．5均使细胞内MDA和Ca^2 含量升高、GSH含量下降,且对细胞毒性存在时间．效应和剂量．效应关系,(2)PM2．5对各指标的影响仅与处理剂量有关,而与样品种类无关．沙尘暴期间大气PM2．5浓度很高,因而沙尘暴PM2.5的危害作用不可忽视。     

Influence of calcium chloride on the thermal behavior of heavy and alkali metals in sewage sludge incineration

In order to separate and reuse heavy and alkali metals from flue gas during sewage sludge incineration, experiments were carried out in a pilot incinerator. The experimental results show that most of the heavy and alkali metals form condensed phase at temperature above 600 degrees C. With the addition of 5% calcium chloride into sewage sludge, the gas/solid transformation temperature of part of the metals (As, Cu, Mg and Na) is evidently decreased due to the formation of chloride, while calcium chloride seems to have no significant influence on Zn and P. Moreover, the mass fractions of some heavy and alkali metals in the collected fly ash are relatively high. For example, the mass fractions for Pb and Cu in the fly ash collected by the filter are 1.19% and 19.7%, respectively, which are well above those in lead and copper ores. In the case of adding 5% calcium chloride, the heavy and alkali metals can be divided into three groups based on their conversion temperature: Group A that includes Na, Zn, K, Mg and P, which are converted into condensed phase above 600 degrees C; Group B that includes Pb and Cu which solidify when the temperature is above 400 degrees C; and Group C that includes As, whose condensation temperature is as low as 300 degrees C.