氧化还原介体催化强化污染物厌氧降解研究进展

 由于厌氧生物处理技术具有产生剩余污泥少、可回收能源等优点而被广泛用于处理各种有机污染物，尤其在有毒、有害、难降解污染物的去除方面取得了良好的效果。然而，厌氧生物法的处理速率通常比较低，而氧化还原介体可通过自身不断的氧化和还原来传递电子，提高电子在氧化还原反应过程中的传递速率，从而促进污染物高效厌氧降解。醌类物质和腐殖酸是应用较多的氧化还原介体，在催化难降解污染物降解方面取得了一定效果。讨论了氧化还原介体的特点、作用机制，并总结了其对偶氮染料厌氧脱色、反硝化和多氯联苯厌氧降解的强化作用，提出了氧化还原介体未来的研究方向。     

n个Schrodinger算子积自伴域

本文讨论了由微分算式l=-d2/dt2 q(t)生成的具有某种边界条件的n个正则Schrodinger算子Li(i=1,…,n)的积Ln…L2L1自伴性问题,证明了积算子Lm…L2L1自伴的充分必要条件为=L*n 1-i(i=1,…,[n 1/2]).     

产品竞争力的分析方法

为了提高产品的市场竞争力，必须采取一定的方法对产品进行竞争力分析。本文提出了一种实用的、基于客户价值的产品竞争力分析方法，该方法通过产品量化的客户感知价值和客户感知成本的组合比较，确定了产品的相对竞争力。     

湖南山丘区景观生态系统退化特征初探

湖南山地丘陵面积约占全省土地总面积的２／３，是省域最重要的景观生态系统类型。自然状态下，湖南山丘区景观生态系统中景观组分性质优良，景观要素组合协调，景观生态过程稳定，景观功能较强。然而，在长期的人类活动影响之下，湖南山丘区景观生态系统显现出明显的退化特征，具有表现为景观要素组合关系改变、景观组分性质劣化、景观生态过程逆转、景观生态系统抗性降低。     

作业成本法对传统成本法的影响分析

介绍了作业成本法的特点,从5个方面探讨了作业成本法与传统成本法的差别,指出作业成本法具有一定的先进性。     

AgCl膜光催化降解色素的研究

利用AgCl膜在不同波长光照条件下对水溶液中的5种有机色素进行催化降解实验．实验结果表明，30min内，5种色素(质量浓度为20mg/L)均得到迅速光解，且在太阳光光照条件下AgCl膜具有非常高的光催化性能．并进一步研究了成膜原料液的浓度对光解率的影响、溶液初始质量浓度与光解速率的关系及悬浮态AgCl的光催化对比实验．     

SnO2@TiO2纳米粒子的光催化性能

以纳米SnO2·nH2O胶体粒子为基质,采用活性层包覆法制备出复合光催化剂SnO2@TiO2.用其对有机磷农药DDVP的稀释液进行降解,并用SEM、TEM、XRD、BET和XPS等手段进行了表征.结果表明:SnO2@TiO2粒径在12nm左右,比表面积为72.27m2g,由锐钛型TiO2与金红石型SnO2组成,光催化活性明显优于单一的SnO2、TiO2.其最佳用量为3.0gL,并且可重复使用.添加剂H2O2、Fe3+的最佳浓度分别为1.65mmolL和0.5mmolL.     

Coastal wetland in South China： Degradation trends, causes and protection countermeasures

There are abundant coastal wetlands in South China and their main characters are the tidal flats, mangroves and coral reefs. In this paper, the status quo of coastal wetlands in South China is introduced and their degradation trends in the last decades are analyzed based on the existing literatures and information. Their degradation trends are characterized by reduction of coastal wetlands＇ area, pollution of seawater environment, degeneration of ecological environment, sharp decrease of biodiversity in the wetlands and so on. At the same time, the causes resulting in the above-mentioned degradations are discussed, mainly concluding imperfect systems of management and legislation, deficient property and assessment systems of the wetlands, weak consciousness of protecting coastal wetlands, shortage of basic study and backward management level and so on. Some countermeasures are put forward for the sake of a sustainable use of the coastal wetlands of South China, mainly including establishing and perfecting administrative and legal systems for the coastal wetlands, developing the study on assessment of coastal wetland, heightening the consciousness of public participation, and strengthening scientific research and establishment of wetland nature reserves.     

Starch-binding domains in the post-genome era

Starch belongs to the most abundant biopolymers on Earth. As a source of energy, starch is degraded by a large number of various amylolytic enzymes. However, only about 10% of them are capable of binding and degrading raw starch. These enzymes usually possess a distinct sequence-structural module, the so-called starchbinding domain (SBD). In general, all carbohydrate-binding modules (CBMs) have been classified into the CBM families. In this sequence-based classification the individual types of SBDs have been placed into seven CBM families: CBM20, CBM21, CBM25, CBM26, CBM34, CBM41 and CBM45. The family CBM20, known also as a classical C-terminal SBD of microbial amylases, is the most thoroughly studied. The three-dimensional structures have already been determined by X-ray crystallography or nuclear magnetic resonance for SBDs from five CBM families (20, 25, 26, 34 and 41), and the structure of the CBM21 has been modelled. Despite differences among the amino acid sequences, the fold of a distorted β-barrel seems to be conserved together with a similar way of substrate binding (mainly stacking interactions between aromatic residues and glucose rings). SBDs have recently been discovered in many non-amylolytic proteins. These may, for example, have regulatory functions in starch metabolism in plants or glycogen metabolism in mammals. SBDs have also found practical uses. Received 25 May 2006; received after revision 26 June 2006; accepted 3 August 2006