n-TiO2光催化机理及其在环境保护中的应用研究进展

本文对半导体二氧化钛的光催化机理、载体形式、反应器等方面的研究进展作了详细概述。并就其在废水处理、杀菌消毒等环境保护方面中的应用作了综述     

一种新型复合球填料在低浓度污再生回用中的应用研究

新型复合球填料为沸石与悬浮球填料的有机组合体，密度约为0．92～0．97g／cm^3，比表面积为711～1185m^2/m^2，表面粗糙，物化性能稳定。在曝气量为20：1，停留时间为6h时，装有新型复合球填料的反应柱挂膜容易，成膜时间短，膜不易脱落，且生物相丰富。膜成熟时对生活污水中的氨氮和COD都有很好的去除效果，出水氨氮浓度≤2mg／L，去除率≥93％；出水COD浓度≤22mg／L，去除率≥80％。新型复合球反应柱在稳定状态处理低浓度的二级出水时，出水氨氮浓度≤2mg／L，去除率89％，出水COD浓度为10～36mg／L，去除率为48％～81％。出水水质符合GB50335-2002标准。     

中和共沉淀法形成铁氧体微晶及其对重金属离子的并合

本文对中和共沉淀法Fe_3O_4生成过程中重金属离子并合程度及其影响因素进行了研究,在实验条件下,发现重金属离子在Fe_3O_4晶格中的并合与其离子半径、电负性和外层电子分布等因素有关。并合程度为:Cu~(2+),CO~(2+),Fe~(2+)>Mn~(2+),Zn~(2+)>Ni~(2+),Cd~(2+),当Fe~(2+)/Fe~(3+)=0.5,pH=9.5±0.5时,对40mgCu~(2+),总铁量(Fe~(2+)+Fe~(3+))2.5g为最小投料量,其并合率可达99.7％以上,相同条件下CO~(2+)并合率大于99.7％,其它重金属离子由于本征特性影响,并合率各不相同,工艺条件适合于污水中Cu~(2+)和Co~(2+)的有效去除,对Mn~(2+),Zn~(2+)的去除也有一定效果,从沉渣的XRD物相分析可知,重金属离子在Fe_3O_4中的并合,是以尖晶石型结构取代式固溶体组成完成的。     

不同生物脱臭填料生物膜成长特性

用活性炭、浮石、陶粒和瓷环分别作为生物滴滤填料进行去除N2S恶臭气体的对比研究。活性炭和浮石对高效脱臭菌有强的吸附和固定作用，挂膜时间短，生物含量高而陶粒和瓷环固定期长，成膜较晚。在循环液流量为24L／h，气流量为0．5m^3／h，进气浓度在500mg／m^3的条件下，活性炭、浮石、陶粒和瓷环的成熟生物膜对H2S的去除率分别为99％、98％、95％和93％，从成膜到发生严重堵塞的生物增量的最大值分别是19．7、70．5、68．9、90．3mg／cm^3。试验对比结果表明，多孔浮石是优质的生物滴滤填料。     

植物吸收环境中金属元素的动力学模型

植物吸收金属元素的过程主要是一个主动吸收过程。目前用离子载体学说解释离子主动吸收过程已经得到了广泛的认同 ;而且各种各样的酶参与了植物主动吸收金属离子的过程。本文对利用酶促反应动力学描述植物吸收环境中金属元素这一现象的可行性及应用现状作了讨论。     

CANON生物膜载体储存及活性恢复研究

采用不同活性恢复手段研究了短期低温（20d,15℃）储存及常温（25℃）低负荷运行后,CANON-MBBR反应器的活性恢复效果.结果显示,CANON悬浮载体经短期低温储存后,通过先恢复温度后缓慢提高进水负荷的方式可使其TN去除负荷恢复率达到102%.若在温度未恢复的基础上直接将进水负荷提升至原水平运行,CANON悬浮载体生物膜将无法维持正常的EPS含量而易发生脱膜现象,致使TN去除负荷恢复率仅为84%.另外,系统有一定基质浓度的基础上,经过25d常温（25℃）低负荷SBR运行后,通过同样的恢复手段可使TN去除负荷恢复率达到96%.通过微生物菌群分析,确定CANON-MBBR系统中功能微生物优势菌属分别为Nitrosomonas和Candidatus Kuenenia,采取合适的恢复手段使系统进入稳定运行阶段后,两者丰度均可分别达到11%以上及27%以上,且悬浮载体脱膜并未对微生物组成造成明显影响.     

LNG船舶锚泊安全距离定量计算建模

为保障液化天然气船舶(LNG船舶)锚泊安全,提出了一种基于船舶漂移运动和船舶碰撞风险的锚泊安全距离计算方法.首先,结合船舶运动数学模型,通过蒙特卡洛模拟LNG船舶走锚漂移运动,得出走锚漂移方向概率密度函数,从而确定船舶走锚漂移横向、纵向距离;同时,结合船舶碰撞概率模型、船舶碰撞损害模型和LNG火灾模型,建立LNG船舶碰撞风险模型,确定满足碰撞概率和风险可接受的安全距离.最后,比较两种模型计算结果,并取其较大值作为LNG船舶锚泊安全距离.结果表明,LNG船锚泊安全距离不仅与环境水域的风、流情况有关,还与附近水域内船舶大小及速度有关.建议交通管理中需结合水域环境特征和水域船舶特点确定LNG船舶的锚泊安全距离.     

The effect of landfill leachate composition on organics and nitrogen removal in an activated sludge system with bentonite additive

A pre-denitrification activated sludge system (AS) without internal recycle was used in lab-scale studies of landfill leachate treatment. A bentonite supplement at a ratio of 1:4 (mineral : biomass) was used to ensure high sludge settling levels and to serve as a micro-organisms carrier. The system was operated within different parameters such as hydraulic retention time (HRT), ammonia loading rate (ALR) or external recycle ratio, which was adapted to treat varying leachate concentrations of COD and ammonia, ranging from 1020 to 2680 mgO(2)l(-1) and 400-890 mgNH(4)-Nl(-1) respectively. The nitrification was complete and ammonia oxidation reached 99%; this was obtained while the ALR did not exceed 0.09 g NH(4)(+)-Ng(-1)MLVSS d(-1) and HRT was not lower than 1 day (in the aeration reactor). The performance of denitrification was successfully improved by controlling the external recycle rate, when the BOD(5)/N ratio in the raw leachate was 4.1. Consequently, N-removal of up to 80% was achieved. A 10-fold decrease in the denitrification rate was obtained at a BOD(5)/N ratio of 0.5. The efficiency of COD removal varied significantly from 36% to 84%. The positive effect of bentonite addition was determined and is discussed based on preliminary studies. The experiments were carried out in fill-and-draw activated sludge with bentonite; the biomass ratio was 1:2. The activated sludge with bentonite was fed with a synthetic high ammonia and organic-free medium.     

Growth substrate selection and biodegradation of PCP by New Zealand white-rot fungi

Nine New Zealand native white-rot fungi were studied for their ability to grow and survive on different substrates formulated from bark, wheat straw, sawdust, apple pomace and maize products in order to identify their pentachlorophenol (PCP) biodegradation potential and to select a fungal carrier for bioaugmentation of polluted soils. Isolates were also evaluated to mineralize (14)C-PCP in liquid culture and in soil. The American fungus Phanerochaete chrysosporium outgrew the native fungi on the substrates tested, but the high colonisation did not result in superior PCP dechlorination as measured by chloride release. Whilst Trametes versicolor inocula produced on wheat straw and SCS (sawdust-corn meal-starch-mix) gave the highest chloride release, colonization of these two substrates as measured by biological potential was lower compared to the pomace and pomace-sawdust-mix. Neither lignin peroxidase nor manganese peroxidase production were measured for New Zealand white-rot fungi during the experiments. Laccase was the only enzyme detected. In liquid culture, the mineralisation rate was higher for T. versicolor isolates compared to P. chyrysoporium. Very little to no pentachloroanisole (PCA) was captured in the volatile fraction of T. versicolor isolates, whereas 75% of the volatile fraction of P. chrysosporium consisted of PCA. The soil microcosms studies, using contaminated soil from a timber treatment site, clearly showed that the New Zealand T. versicolor isolates mineralized PCP. Degradation of PCP in non-sterile soil was higher in the presence of white-rot fungi than in soil without white-rot fungus. This demonstrates that viable white-rot fungus is necessary for significant PCP degradation and that T. versicolor isolates showed PCP remediation potential. Wheat straw and SCS could be suitable carriers for New Zealand native T. versicolor isolates for bioremediation of PCP polluted soil sites.     

利用固定化细胞技术处理废水研究进展

固定化细胞技术是一门新兴的废水处理技术。与固定化酶技术相比,固定化细胞技术保持了原有的多酶系统,对于需要多酶顺序作用的反应更具优势,且不需要辅酶再生。其缺点是必须使用胞内酶,且难以去除细胞内的“副作用”酶。介绍了目前常见的四类固定化方法(即吸附法、包埋法、共价结合法和交联法)、三类固定化细胞载体材料(即有机高分子载体、无机载体和复合载体)以及该方法在废水处理中的应用,并提出了在应用中有待解决的问题。