pH值对好氧颗粒污泥同步硝化反硝化过程的影响

从反应器脱氮性能和好氧颗粒污泥理化性状方面研究了pH值对好氧颗粒污泥同步硝化反硝化脱氮过程的影响.结果表明,好氧颗粒污泥微生态环境的形成,大大增强其耐酸碱冲击负荷能力,在pH值8～9范围内氨氮去除率均达到95%以上.在pH值6～9范围内,好氧颗粒污泥理化性状稳定,没有发生解体现象.     

浅谈河道与水库清淤的新工艺

分析比较了传统河道水库淤积的清除工艺 ,从而提出一种新型的清淤技术 ,即气举与自激振荡脉冲水射流联合作用下的清淤工艺。分析了这种新工艺的清淤原理 ,论证了其对水下坚硬沉积物的破碎与抽取的连续作用机理 ;研究了空压机的工作压力与清淤量的关系。     

A novel biosorbent: characterization of the spent mushroom compost and its application for removal of heavy metals

The spent mushroom compost of Lentinus edodes was used as a biosorbent for adsorbing cadmium, lead and chromium from solutions under batch conditions for the first time. Titration of the biomass revealed that it contained at least three types of functional groups. The Fourier transform infrared spectrometry showed that the carboxyl, phosphoryl, phenolic groups were the main groups. The simulated values of pK, and molar quantity were 5.00 and 0.44 mmol/g, 7.32 and 1.38 mmol/g, 10.45 and 1.44 mmol/g, respectively. The biosorption ability increased with pH in acid condition. When 10 mg/L biomass dosage was added in, there was no significant increment of metal uptake. The maximum uptake estimated with the Langmiur isotherm model were 833.33 mg/g for Cd（ Ⅱ ）, 1000.00 mg/g for Pb（ Ⅱ ） and 44.44 mg/g for Cr（ Ⅲ ）, respectively. All the results showed that vast potential sorption capacity was existed in the biomass for adsorbing these three kinds of metals studied.     

烟气条件对直流电晕自由基簇射NO氧化过程的影响

运用以湿空气为自由基源物质的直流电晕自由基簇射系统,研究了烟气在反应器内的滞留时间、烟气流速和NO浓度对NO氧化过程的影响.结果表明:烟气流速的增加会抑制电晕放电的发展,而烟气中NO浓度的增加则使放电变得更加容易.NO的氧化受烟气在反应器内滞留时间的影响较小,而它受烟气流速的影响较大.在2W的输入功率下,当烟气在反应器内的滞留时间从8.5s增加到34.2s时,NO的氧化率只从54.5 %提高到57.6 %.而在1.7W·h/m³的能量密度下,当烟气流速从1.4cm/s增加到6.3cm/s时,NO的氧化率从60.0%减少到38.6%,能量利用率也从20.8g/(kW·h)下降到了13.3g/(kW·h).在湿空气流量一定的情况下,NO初始浓度存在一个最佳值,本实验中最佳的NO浓度为100×10^-6左右.     

生物除磷过程厌氧释磷的代谢机理及其动力学分析

运用充分曝气后的好氧末端活性污泥进行了厌氧释磷实验.结果表明,在厌氧释磷过程中VSS呈现出上升的趋势,而MLSS及灰分均呈现出下降的趋势.当微生物体内的糖原耗尽时,会引起厌氧吸收HAc及释磷过程的中断.得出ΔρPΔρPHB、ΔρGLYΔρPHB、ΔρPΔCOD、ΔρPHBΔCOD各比值的平均值分别为0.48、0.50、0.44、0.92.通过对厌氧吸收HAc及释磷动力学过程进行模拟,得到QHAc,max为164mg·g-1·h-1,QP,max为69.9mg·g-1·h-1,KGYL为0.005,KCOD为3mg·L-1.ΔρPΔCOD与溶液中pH呈明显的线性关系,且得到了二者之间的线性方程.     

污水生物处理过程药品及个人护理品转化产物识别研究进展

药品及个人护理品(pharmaceuticals and personal care products,PPCPs)在污水生物处理过程会发生生物及化学转化从而生成转化产物,某些转化产物较母体化合物毒性更高.目前对PPCPs转化产物关注不够,转化产物识别方法不明确.本文介绍了污水中PPCPs转化产物的识别流程,系统阐述了...     

重庆银莲花属药用植物资源研究

经调查鉴定,重庆银莲花属药用植物有10种4变种。重点介绍了其医疗用途、地理分布、资源状况及其开发前景,为进一步开发利用我市丰富的银莲花属植物资源提供了科学依据。     

沼泽红假单胞菌W12对活性黑5的厌氧脱色和降解作用

从处理印染废水的厌氧移动床生物膜反应器（moving bed biofilm reactor, MBBR）中分离到一株具有高效脱色活性的沼泽红假单胞菌W12。经实验确定W12对活性黑5（reactive black 5,RB5）脱色的适宜条件为：pH＜10;有光照;谷氨酸盐或乳酸盐作为碳源,当乳酸钠为碳源时浓度应＞500 mg/L;盐度不超过5％;RB5浓度不大于700 mg/L。紫外可见光谱扫描结果表明,RB5的脱色和降解过程生成芳香胺类化合物,这些中间产物可进一步降解。此外发现,RB5诱导生成的胞外代谢物能提高W12的脱色活性。     

上海与伦敦城市绿地的生态功能及管理对策比较研究

在资料收集及实地采样调查的基础上 ,文章对上海与伦敦城市绿地的生态功能及管理对策进行了比较分析 ,指出了上海城市绿地建设及管理中的一些优点及不足之处。     

Modulation of steroidogenesis by coastal waters and sewage effluents of Hong Kong, China, using the H295R assay

BACKGROUND, AIM, AND SCOPE: The presence of a variety of pollutants in the aquatic environment that can potentially interfere with the production of sex steroid hormones in wildlife and humans has been of increasing concern. The aim of the present study was to investigate the effects of extracts from Hong Kong marine waters, and influents and effluents from wastewater treatment plants on steroidogenesis using the H295R cell bioassay. After exposing H295R cells to extracts of water, the expression of four steroidogenic genes and the production of three steroid hormones were measured. MATERIALS AND METHODS: Water samples were collected during the summer of 2005 from 24 coastal marine areas and from the influents and effluents of two major waste water treatment plants (WWTPs) in Hong Kong, China. Samples were extracted by solid phase extraction (SPE). H295R cells were exposed for 48 h to dilutions of these extracts. Modulations of the expression of the steroidogenic genes CYP19, CYP17, 3betaHSD2, and CYP11beta2 were determined by measuring mRNA concentrations by real-time polymerase chain reaction (Q-RT-PCR). Production of the hormones progesterone (P), estradiol (E2), and testosterone (T) was quantified using enzyme linked immunosorbent assays (ELISA). RESULTS: Extracts from samples collected in two fish culture areas inhibited growth and proliferation of H295R cells at concentrations greater or equal to 10(5) L equivalents. The cells were exposed to the equivalent concentration of active substances in 10,000 L of water. Thus, to observe the same level of effect as observed in vitro on aquatic organisms would require a bioaccumulation factor of this same magnitude. None of the other 22 marine samples affected growth of the cells at any dilution tested. Twelve of the marine water samples completely inhibited the expression of CYP19 without affecting E2 production; inhibition of CYP17 expression was observed only in one of the samples while expression of CYP11beta2 was induced as much as five- and ninefold after exposure of cells to extracts from two locations. The expression of the progesterone gene 3betaHSD2 was not affected by any of the samples; only one sample induced approximately fourfold the production of E2. Although more than twofold inductions were observed for P and T production, none of these values were statistically significant to conclude effects on the production of these two hormones. While influents from WWTPs did not affect gene expression, an approximately 30% inhibition in the production of E2 and a 40% increase in P occurred for the exposure with influents from the Sha Tin and Stonecutters WWTPs, respectively. Effluents from WWTPs did not affect the production of any of the studied hormones, but a decrement in the expression of the aldosterone gene CYP11beta2 was observed for the Sha Tin WWTP exposure. No direct correlation could be established between gene expression and hormone production. DISCUSSION: Observed cytotoxicity in the two samples from fish culture areas suggest the presence of toxic compounds; chemical analysis is required for their full identification. Although effluents from WWTPs did not affect hormone production, other types of endocrine activity such as receptor-mediated effects cannot be ruled out. Interactions due to the complexity of the samples and alternative steroidogenic pathways might explain the lack of correlation between gene expression and hormone production results. CONCLUSIONS: Changes observed in gene expression and hormone production suggest the presence in Hong Kong coastal waters of pollutants with endocrine disruption potential and others of significant toxic effects. The aromatase and aldosterone genes seem to be the most affected by the exposures, while E2 and P are the hormones with more significant changes observed. Results also suggest effectiveness in the removing of compounds with endocrine activity by the WWTPs studied, as effluent samples did not significantly affect hormone production. The H295R cell showed to be a valuable toll in the battery required for the analysis of endocrine disrupting activities of complex environmental samples. RECOMMENDATIONS AND PERSPECTIVES: Due to the intrinsic complexity of environmental samples, a combination of analytical tools is required to realistically assess environmental conditions, especially in aquatic systems. In the evaluation of endocrine disrupting activities, the H295R cell bioassay should be used in combination with other genomic, biological, chemical, and hydrological tests to establish viable modes for endocrine disruption and identify compounds responsible for the observed effects.