水生植物生物能在苏州市CO2减排中的作用

苏州市的CO2排放量在逐年上升,CO2减排工作任务艰巨。开发无污染的新能源替代化石燃料是CO2减排的一种思路。苏州作为一个江南水乡城市,水资源丰富,水生植物生长旺盛。主要探讨了水生植物(包括藻类和水葫芦)生物能在苏州市CO2减排中的作用。通过粗略估算,藻类和水葫芦产生的年生物能(折算为标准煤)1 200.35万t,大约占苏州年总能耗的四分之一,即可以减少大约四分之一的CO2排放。因此,水生植物生物能在苏州市CO2减排中具有重要的作用。     

Concurrent catalytic removal of typical volatile organic compound mixtures over Au-Pd/α-MnO2 nanotubes

α-MnO_2 nanotubes and their supported Au-Pd alloy nanocatalysts were prepared using hydrothermal and polyvinyl alcohol-protected reduction methods, respectively. Their catalytic activity for the oxidation of toluene/m-xylene, acetone/ethyl acetate, acetone/m-xylene and ethyl acetate/m-xylene mixtures was evaluated. It was found that the interaction between Au-Pd alloy nanoparticles and α-MnO_2 nanotubes significantly improved the reactivity of lattice oxygen, and the 0.91 wt.% Au0.48 Pd/α-MnO_2 nanotube catalyst outperformed the α-MnO_2 nanotube catalyst in the oxidation of toluene, m-xylene, ethyl acetate and acetone. Over the0.91 wt.% Au0.48 Pd/α-MnO_2 nanotube catalyst,(i) toluene oxidation was greatly inhibited in the toluene/m-xylene mixture, while m-xylene oxidation was not influenced;(ii) acetone and ethyl acetate oxidation suffered a minor impact in the acetone/ethyl acetate mixture; and(iii) m-xylene oxidation was enhanced whereas the oxidation of the oxygenated VOCs(volatile organic compounds) was suppressed in the acetone/m-xylene or ethyl acetate/m-xylene mixtures. The competitive adsorption of these typical VOCs on the catalyst surface induced an inhibitive effect on their oxidation, and increasing the temperature favored the oxidation of the VOCs. The mixed VOCs could be completely oxidized into CO_2 and H_2 O below 320°C at a space velocity of 40,000 m L/(g·hr). The 0.91 wt.% Au0.48 Pd/α-MnO_2 nanotube catalyst exhibited high catalytic stability as well as good tolerance to water vapor and CO_2 in the oxidation of the VOC mixtures. Thus, the α-MnO_2 nanotube-supported noble metal alloy catalysts hold promise for the efficient elimination of VOC mixtures.     

硝化悬浮填料塔中氨氧化细菌群落稳定性特征分析

利用PCR-DGGE分析技术,对于化学生物絮凝处理工艺中悬浮填料塔的氨氧化细菌(AOB)群落进行了研究。主要考察了曝气强度和水力停留时间2个运行参数调整的情况下,系统AOB群落结构的变化。生物膜样品直接取自硝化填料塔,多维尺度(MDS)方法用于DGGE电泳图谱的分析,分析结果以二维图形向量的方式显示,结果表明,曝气强度和水力停留时间均对AOB群落有一定的影响,主要的AOB种类在运行过程中基本不变,系统对于运行条件具有良好的稳定性。     

上海市大气污染物排放现状评价、预测及对策研究

通过对1985-2001年间上海市大气污染物排放情况的考察,分析了SO2排放强度和人均SO2排放量等大气污染物排放指标变化的原因;与国内主要城市和美国的大气污染物排放指标对比情况表明,上海市大气污染物排放强度在国内处于较低的水平,但与发达国家相比还有较大差距;采用Sigmoid模型对上海市大气污染物排放进行了预测;提出了降低大气污染物排放的几点对策.     

以法矫正企业行为

从2004年初的川化沱江污染到2005年末的吉化松花江污染和广东韶关冶炼厂北江污染,无不令国人瞩目。甚至引起国际关注。三起污染事件影响的人群从数十万到数百万不等。仅川化沱江污染就导致近百万群众饮水中断达26天,直接经济损失约3亿元。沱江生态环境遭受严重破坏,据专家估计,需要5年时间才能恢复事故前水平。（华西都市报）     

Present status and changes of the phytoplankton community after invasion of Neosalanx taihuensis since 1982 in a deep oligotrophic plateau lake, Lake Fuxian in the subtropical China

Phytoplankton assemblages in the subtrophical oligotrophic Lake Fuxian, the second deepest lake in China, were investigated monthly from September 2002 to August 2003. A total of 113 species belonging to seven phyla were identified, among them, a filamentous green alga, Mougeotia sp., dominated almost throughout the study period and comprised most of the total phytoplankton biomass.Mougeotia sp. has made a substantial development during the past decades: it was absent in 1957, only occasionally present in 1983,increased substantially in 1993, and became predominant in 2002--2003. It is likely that natural invasion of the Taihu Lake noodlefish (Neosalanx taihuensis) has led to a change of dominant herbivorous zooplankton from small to large calanoid, which has increased grazing pressure on small edible algae, and thus has indirectly favored the development of the inedible filamentous Mougeotia sp.     

Mobility and sulfidization of heavy metals in sediments of a shallow eutrophic lake, Lake Taihu, China

The technique of DGT (diffusive gradients in thin films) using three diffusive gel thicknesses was applied to estimate the mobility and bioavailability of heavy metals in sediments and porewater of Lake Taihu, China. The DGT results showed significantly positive correlations between Co, Pb, Cd and Mn, and Ni and Fe concentrations in porewater. Cu and Zn showed a significantly negative correlation with Mn, due to Cu combination with carbonates and Zn derived from agricultural pollution, respectively. The rank order of average concentrations of Co, Ni and Cd at each station was DGT_1.92 > DGT_0.78 > DGT_0.39, suggesting stronger resupply from sediments to porewater when using thicker diffusive gels. Comparing centrifugation and DGT measurements, Co, Ni and Cd are highly labile; Mn and Fe are moderately labile; and Cu, Zn and Pb are slightly labile. The variations of AVS concentrations in sediment cores indicate that metal sulfides in deeper layers are easily diffused into surface sediments.     

周丛藻类水质处理系统中氮、磷污染物去除效果研究

为了评价周丛藻类系统对受污染景观河道水体氮、磷污染物处理效果,以及最佳污染物去除浓度,通过设置周丛藻类水质处理系统,并模拟藻类自然生长条件,于2006年夏秋之季,对该周丛藻类系统的水质处理效果进行了研究.结果表明,①相对于标准培养液条件下20%的平均去除率,周丛藻类水质处理系统中TN、NH4 -N去除率分别可达30%和50%以上,其中TP平均去除率则相对较低(＜10%);②系统最大氮污染物去除率(TN＞65%,NH4 -N＞80%)出现在进水TN浓度约11.0mg·L-1条件下,而TP去除率则随进水浓度增加呈下降趋势;③试验期间,系统中周丛藻类生物量增加54%,Chl-a浓度增加58.2%,同时藻类群落由试验初期的颗粒态硅藻、绿藻为主,演替为以丝状和颗粒状蓝、绿藻为主.     

加速能源转型与产业结构调整的环境健康协同效益评估：以京津冀鲁地区为例

京津冀鲁地区是我国温室气体减排与大气污染治理的重心,随着末端控制措施减排空间的缩紧,通过能源转型和产业结构优化等源头治理方式实现减污降碳协同增效的需求日益迫切.基于开发的REACH综合评估模型,通过情景模拟分析,评估了京津冀鲁地区进一步加强末端控制的减排潜力,以及加速能源转型与产业结构调整的环境和健康协同效益.结果表明,未来在京津冀鲁地区快速推行最佳可行的末端控制技术,2035年能够带来约3.3μg·m^-3的PM_2.5浓度削减,但仅依靠此措施不足以实现区域PM_2.5浓度控制目标;加速能源转型和产业结构调整是京津冀鲁地区实现空气质量达标的必要条件,2035年,能源经济系统的加快转型对大气PM_2.5污染改善的贡献可达6.3μg·m^-3;相比于当前的政策力度,4省市虽然需要额外付出相当于地区GDP 0.9%～2.5%的社会经济成本以实现PM_2.5浓度控制目标,但加速转型带来的环境健康协同效益能够部分或全部覆盖该成本.     

厌氧水解酸化-好氧氧化A1/A2/O工艺剩余污泥减量

在碱减量印染废水A₁/A₂/O生物处理系统,通过污泥回流、把剩余污泥回流到A₁段,利用A段污泥的水解、酸化和O段微生物的好氧氧化作用可有效实现对回流剩余污泥的减量,同时O段好氧污泥的表观产率系数下降,系统产生的剩余污泥量减少.厌氧水解酸化-好氧氧化A₁/A₂/O工艺实现污泥减量由3段共同完成:A₁段实现回流剩余污泥的“液化”和惰性化;A₂段对系统污泥减量起到了强化作用;而O段微生物的合成作用在逐渐减弱.6个月连续运行的动态试验表明,在A₁段的容积负荷(COD_Cr)为2.54 kg·(m³·d)^-1、水力停留时间为7.56h条件下,A₁段利用水解酸化作用对回流剩余污泥的减量达到67.87%,系统O段好氧污泥的表观产率系数也下降到试验初始时的45.5%.在A₁/A₂/O污泥减量系统中,各段污泥性状发生了变化,A₁段污泥[MLVSS/MLSS]值从试验开始时的0.718 2下降到0.592 2,A₂段污泥[MLVSS/MLSS]值从0.667 3下降到0.526 7,剩余污泥的减量是活性污泥逐渐惰性化过程,污泥的粒度分析也证明了这一点.