泉州湾滩涂沉积物对Cu（Ⅱ）的吸附实验

研究了Cu(Ⅱ)在泉州湾滩涂沉积物上的吸附行为。探讨了pH和温度对吸附作用的影响，测定了其吸附等温线。实验结果表明，常温下Cu(Ⅱ)在泉州湾滩涂沉积物上的吸附平衡时间约需3．5小时；吸附量随pH的升高先增大而后减少，pH=6．0左右时达最大；吸附量随温度的升高而增大；其吸附行为可以很好地用Langmuir型吸附等温线来描述。并在此基础上初步探讨了Cu(Ⅱ)在泉州湾滩涂沉积物上的吸附机理。     

测空气中SO2时的主要影响因素

目前测定空气中SO2主要采用甲醛吸收-副玫瑰苯胺分光光度法。该法操作比较严格，测试结果的准确度受诸多因素的影响。因此文中对这些影响因素进行了探讨，主要为试剂质量、显色温度和显色时间、溶液加入顺序、比色皿、空气采样器流量、采样温度、导气管的吸附等因素对测定结果的影响进行了探讨。     

Carbon Dioxide Balance of Wood Substitution: Comparing Concrete- and Wood-Framed Buildings

In this study a method is suggested to compare the net carbon dioxide (CO₂) emission from the construction of concrete- and wood-framed buildings. The method is then applied to two buildings in Sweden and Finland constructed with wood frames, compared with functionally equivalent buildings constructed with concrete frames. Carbon accounting includes: emissions due to fossil fuel use in the production of building materials; the replacement of fossil fuels by biomass residues from logging, wood processing, construction and demolition; carbon stock changes in forests and buildings; and cement process reactions. The results show that wood-framed construction requires less energy, and emits less CO₂ to the atmosphere, than concrete-framed construction. The lifecycle emission difference between the wood- and concrete-framed buildings ranges from 30 to 130 kg C per m² of floor area. Hence, a net reduction of CO₂ emission can be obtained by increasing the proportion of wood-based building materials, relative to concrete materials. The benefits would be greatest if the biomass residues resulting from the production of the wood building materials were fully used in energy supply systems. The carbon mitigation efficiency, expressed in terms of biomass used per unit of reduced carbon emission, is considerably better if the wood is used to replace concrete building material than if the wood is used directly as biofuel.     

On-line optical determination of floc size of Fe(Ⅲ) coagulants

This study investigated the floc aggregation, average floc size, floc size variance and floc growth velocity when ferric chloride （FeCl3） and polyferric chloride （PFC） were used to treat the simulated water samples. The factors including coagulant dose, ionic strength and solution pH, which affect the floc aggregation, were studied. Experiments were carried out in a bench-scale reactor using photometric dispersion analyzer （ PDA）. Results showed that there were great differences between the floc aggregation of PFC and FeCl3. The average floc size and fioc growth velocity of PFC were much larger than those of FeCl3. Compared with FeCl3, PFC gave a better coagulation performance in wider range of pH, dosage and ionic strength. It was also found that the coagulation efficiency of PFC did not depend on average floc size but on floc growth velocity.     

Geological CO2 Storage as a Climate Change Mitigation Option

Carbon dioxide (CO₂₎ capture and storage is increasingly being considered as an important climate change mitigation option. This paper explores provisions for including geological CO₂ storage in climate policy. The storage capacity of Norway's Continental Shelf is alone sufficient to store a large share of European CO₂ emissions for many decades. If CO₂ is injected into oil reservoirs there is an additional benefit in terms of enhanced oil recovery. However, there are significant technical and economic challenges, including the large investment in infrastructure required, with related economies of scale properties. Thus CO₂ capture, transportation and storage projects are likely to be more economically attractive if developed on a large scale, which could mean involving two or more nations. An additional challenge is the risk of future leakages from storage sites, where the government must take on a major responsibility. In institutional and policy terms, important challenges are the unsettled status of geological CO₂ storage as a policy measure in the Kyoto Protocol, lack of relevant reporting and verification procedures, and lack of decisions on how the option should be linked to the flexibility mechanisms under the Kyoto Protocol. In terms of competitiveness with expected prices for CO₂ permits under Kyoto Protocol trading, the relatively high costs per tonne of CO₂ stored means that geological CO₂ storage is primarily of interest where enhanced oil recovery is possible. These shortcomings and uncertainties mean that companies and governments today only have weak incentives to venture into geological CO₂ storage.     

戴明循环理论在规划环评工作程序中的应用初探

通过分析现阶段我国规划环评的现状和存在的问题,结合国内外规划环评及其工作程序的研究成果,提出使用戴明循环理论对现阶段的规划环评工作程序进行改进,使程序层次化、工作细分化,增强整个规划环评工作的可操作性,使规划环评工作落实到单位和人,明确责任,减少部门间冲突.戴明循环理论的引入,提高规划环评的评价效果和效率,为规划环评提供了一个有效科学的评价方法,有助于规划环评的顺利开展,使环境问题从源头上得到控制,适应建设和谐社会的需要.     

纳米TiO2光催化反应器研究进展

光催化氧化作为一种高级氧化技术,在环境工程治理领域得到较快的发展。主要介绍了纳米TiO2光催化反应器近年来的研究进展,对各类型反应器的优缺点进行了深入分析,并展望了催化反应器应用前景。     

采用钙钛矿型催化剂(La0.8K0.2Cu0.05Mn0.95O3)同时催化去除NOx和碳烟的研究

将钙钛矿型催化剂与碳烟均匀混合后置于固定床连续流动反应体系中,利用程序升温反应技术,在模拟柴油机尾气的情况下对同时催化去除氮氧化物(NOx)和碳烟的反应进行了实验研究.通过改变含Cu原料的用量,得到不同Cu取代量的催化剂La0.8K0.2CuxMn1-xO3,性能评价结果表明,La0.8K0.2Cu0.05Mn0.95O3催化剂的综合性能较好,碳烟的起燃温度及NO向N2的最大转化率分别为280℃和58.0%.采用该催化剂,进一步考察了进气中NO浓度、O2浓度、进气总流量及催化剂与碳烟的接触状况对反应的影响.研究结果表明,进气中NO浓度、O2浓度、气体总流量和催化剂与碳烟之间的接触状况对NO的去除率的影响比较明显,而对碳烟起燃温度的影响较小.O2浓度从5%变为7.5%时,碳烟的起燃温度及最大NO转化率分别从280℃和53.8%变为270℃和96.7%.碳烟与催化剂松散接触时,碳烟的起燃温度及最大NO转化率分别为290℃和48.4%,紧密接触时分别为275℃和70.4%.而进气中NO浓度、气体总流量的变化对碳烟的燃烧基本上没有影响,虽然NO的转化率有明显变化,但生成的N2总量基本不变.     

纳米金红石TiO2的转晶及声催化降解偶氮品红的研究

利用超声波结合过氧化氢(H2O2)使纳米金红石型TiO2转晶,制备出了大约含有30%锐钛相的转晶纳米TiO2.通过TiO2催化超声降解偶氮品红的研究证实了转晶纳米TiO2粉末具有明显的声催化活性.除此之外,还考察了各种因素对转晶纳米TiO2催化超声降解偶氮品红反应的影响.结果表明,在转晶纳米TiO2催化剂的作用下,偶氮品红的超声降解效果明显优于使用纳米金红石型和纳米锐钛型TiO2的情况.偶氮品红的声催化降解过程符合一级动力学反应.在超声波频率40 kHz、输出功率50 W、催化剂用量1000 mg·L-1、pH为5.00、温度为20℃、偶氮品红水溶液初始浓度20 mg·L-1的条件下,照射40 min时的降解率即可达到75%以上.     

Ni2+对2-氯酚厌氧降解系统的影响

针对重金属对难降解有毒有机物厌氧降解的影响问题,采用间歇试验法研究Ni2 对2-氯酚(2-CP)厌氧降解系统的影响规律.结果表明,当ρ(Ni2 )＜5 mg/L时,Ni2 对2-CP厌氧降解表现出轻度促进,当ρ(Ni2 )为5～500 mg/L,Ni2 以抑制作用为主,抑制作用随ρ(Ni2 )的增加而增强.Ni2 对原基质及关键中间产物苯酚和苯甲酸的抑制程度表现为:苯酚＞苯甲酸＞2-CP;ρ(Ni2 )低时的驯化能有效提高厌氧污泥对Ni2 毒性的耐受性能,300 mg/L Ni2 对2-CP降解的抑制从驯化前的65%降至驯化后的21%.Ni2 对2-CP厌氧降解的抑制作用与污泥中Ni的截留量之间存在正相关关系.抑制浓度CIP值和方程αC=[1-(I/I*)m]/[1 (I/I*)n)]能较好地表征厌氧生物处理过程受抑制程度.