壳聚糖吸附处理废水的研究进展

壳聚糖吸附处理废水的研究包括其对废水吸附性能和吸附机理的研究两个方面。壳聚糖表现出了良好的吸附废水中重金属离子、染料分子和其它易引起变异物质的能力;壳聚糖对金属离子和染料的吸附机理模型研究理论意义重大,它将进一步推动壳聚糖的实际工程应用。     

染料废水生化处理研究动态

生化法处理染料废水是近年来研究的热点。综述了近年来国内外染料废水生物处理研究的进展，特别对厌氧一好氧联合处理法在脱色和COD去除中的作用、高效菌种的筛选，及其应用方面的各种新技术进行了分析和评述。     

阳离子染料废水治理技术

介绍了阳离子染料废水的特点,以及近年来阳离子染料废水的各种处理技术,并对阳离子染料废水处理技术的发展进行了展望,指出阳离子废水处理技术正朝着各种工艺优化组合的方向发展。     

臭氧高级氧化法处理染料废水的研究

采用臭氧高级氧化技术对某染料废水进行处理,探究不同条件对染料废水COD以及色度的去除效果的影响,确定最佳工艺条件。在最佳条件下,采用单独臭氧、单独紫外、臭氧-紫外、臭氧-双氧水以及臭氧-铁炭五种氧化方法对染料废水进行处理。结果表明:臭氧氧化技术最佳条件为pH值=8,臭氧流量80 L/h,反应时间为2 h;采用最佳处理方案,采用臭氧-紫外高级氧化技术处理染料废水,其脱色率为98.3%,COD去除率为67.0%。     

蒽醌染料活性艳蓝KN-R的化学氧化脱色和矿化

研究了使用NaClO化学氧化处理活性艳蓝KN-R模拟染料废水。分别以592nm、380nm、255nm波长处的吸光值为主要指标,跟踪染料的脱色降解。考察了NaClO投加量、染料浓度、温度和13H值等主要因素对模拟废水脱色的影响。结果表明：用NaClO化学氧化处理0．1mmolL^-1的活性艳蓝KN-R模拟染料废水,当NaClO与染料的摩尔比为18,T=30℃,13H值为7时,反应30分钟,脱色率可达到100％。pH值对脱色和TOC的去除有很大影响,酸性或中性条件下,染料快速脱色,30分钟后吸光值基本恒定,反应6个小时TOC的去除仍不明显;碱性条件下,染料缓慢脱色,但反应6个小时TOC的去除率可以达到40％左右。     

染料废水脱色的物理化学处理技术

染料废水目前主要的脱色方法有吸附、混凝、氧化还原和生化法.活性炭吸附适用于低浓度的染料废水处理.聚硅硫酸铁混凝效果与Fe/SiO4摩尔比和pH值相关.氢氧化镁可有效去除印染废水中的直接红染料.有机絮凝剂往往需要和其它药剂复配.氧化法脱色率大,但成本高昂,且受染料废水的组成、氧化性及pH值影响.还原法药剂价格低廉,但还原降解产物具有毒性,必须经过二次处理.生物法成本较低,又受制于染料的生物降解性.因此发展多种手段联合应用已是当前染料废水处理的研究方向.     

基于硅藻土载体的催化剂的应用研究

在简单论述硅藻土的特性及其作为催化剂载体的特性的基础上,论述了以硅藻土为载体,添加单一的Ti O2、Fe2O3或一些混合物质所制备的复合催化剂在处理染料废水、有机废水、含重金属废水以及含甲醛废气的应用,并展望了该类复合催化剂在制备工艺、材料选取、处理范围以及处理效果方面的发展趋势。     

负载型水处理剂的制备及应用

文章介绍了以多孔材料为载体的负载型水处理剂的制备方法,并分析了水处理剂对油类污染物、含苯基类废水、染料废水、重金属离子废水等的处理效果。通过分析可知,负载后的水处理剂同单一的水处理剂相比具有更好的废水处理效果。     

凤眼莲用于废水净化

初步探讨了凤眼莲在净化废水方面的应用效果,结果表明凤眼莲除对生活污水具有较强的适应能力和净化能力外.在特殊处理后的钻井废水中,也能较正常生长、繁殖并起到一定的净化作用。本文还谈到了废水pH对凤眼莲的影响.对凤眼莲净化废水的机理也作了简述,指出用凤眼莲处理净化废水是一种经济有效的好方法。     

粉煤灰改性吸附材料的研究

本文阐述了粉煤灰的主要化学成份、结构、物理性质，指出粉煤灰改性的物质基础，并结合笔者的研究情况，分析了改性粉煤灰处理废水和废气的机理，介绍了其在处理废水和废气的研究与应用情况，提出了应用改性粉煤灰处理废水和废气中存在的问题及今后研究的重点。     

毕节地区各土类水土保持树种的Fuzzy评价

根据毕节地区16个主要造林树种的生态生物学特性,结合本区气候和土壤生态条件,运用 Fuzzy 二级评价模型,对各土类水土保持树种的适宜程度进行了综合评价。     

贵州生物质能源树种资源的开发利用

根据贵州省生物质能源树种主要分布区线路调查和典型样地调查的结果，介绍了贵州省生物质能源树种的研究现状和存在问题，对贵州的生物质能源树种进行了分类并报道了资源的分布特点。提出了贵州应重点利用现有生物乙醇树种资源，积极稳妥发展生物柴油树种资源，并对开发利用技术和途径进行了探讨。     

山东省迁徙鸟类资源的保护与利用

为了有效保护和利用山东省迁徙鸟类资源．对该省迁徙鸟类的资源现状进行了研究。结果表明，山东省共有迁徙鸟类357种和亚种，占全省鸟类总数的87．9％；夏候鸟84种、占总数的20．7％，冬候鸟47种、占总数的11．6％，旅鸟226种和亚种、占总数的65．7％。其中有67种被列为国家一、二级保护鸟类。威胁该区迁徙鸟类生存的主要因素包括人们的直接破坏、迁徙鸟类栖居地的破坏和环境污染等，并据此提出了相应的保护对策和利用措施。     

济南地区直翅目昆虫资源及其开发利用

本文报道了济南地区直翅目昆虫资源的种类组成，提出为害严重种类、优势种类、传统利用种类及易于捕捉或饲养种类共２４种，可作为本地区开发直翅目昆虫资源的首选类群。根据资源的生物学特性，本文讨论了开发利用的途径与措施     

功能性低聚糖的现状与发展

介绍了功能性低聚糖的现状、生理功能、主要种类、结构、生产、特性及其应用,展望了发展前景。     

中缅边境地区稀有魔芋品种资源研究初探

生长在中缅边境地区的稀有魔芋品种具有与国内外已报道过的品种迥然不同的繁殖特点。该品种除具有魔芋多糖含量高、分子量大和粘度值高的特点外,还具有地下部分的肉质根（球）;不同的是各枝叶交叉点上生长着可供繁殖的小球茎。这一稀有品种至今尚未见报道。     

Compliance of Australian threatened species recovery plans with legislative requirements

Recovery plans are the main documents supporting management decision-making for threatened species. We evaluated Australian recovery plans to assess their appropriateness as conservation and management planning instruments. Six legislative requirements (species information and general requirements, species distribution and location, known and potential threats, objectives, performance criteria and actions, duration of the plan, and estimated costs of plan implementation) were used to assess the degree of compliance of recovery plans with the relevant legislation. We assessed all 236 official recovery plans which had been adopted as at January 2006. The results showed that plans were most compliant regarding the setting of objectives, performance criteria, recovery actions, and duration of plan. Most plans included a single performance criterion that was generally related to the population status of target species. Improvement is required in relation to identification of current threats and critical habitats, and the establishment of basic elements of monitoring and evaluation for measuring recovery progress. Gaps in ecological information are the main factors affecting adequate compliance with legislative requirements as opposed to managerial information (e.g. clarity in establishing the implementation schedule, costs and resource allocation). Planning deficiencies could be addressed by improving the recovery planning guidelines and more carefully reviewing the drafting and adoption of new plans.     

Can Species Have Capabilities,and What if They Can?

In this article, I apply the environmental or expanded capabilities approach to species and examine whether species as wholes can have capabilities and what are the implications if they can. The examination provides support for the claim that species as evolutionary groups can possess capabilities. They have integrity, which refers to the functionings that enable the self-making and development (evolvement) of species, and it is conceptually possible to identify capabilities that essentially enable or contribute to species integrity. One central capability for species can be identified from conservation literature: adaptive capacity, the ability of species to react to environmental changes by self-regulative evolution. After constructing the main argument that species can have capabilities and that they possess the capability to adaptive capacity, I shortly expound on the implications of these claims. It turns out that there are at least three different ways to apply the notion, and that the claim ‘species have capabilities’ does not entail that species are necessarily recipients of justice.     

Strategic Environmental Assessment of Plans and Programs: A Methodology for Estimating Effects on Biodiversity

We developed a methodology for biodiversity evaluations within the process of Strategic Environmental Assessment and we applied it to the estimation of the effect of two Regional Plans of Development on all bird species inhabiting the Castilla y León region (northwestern Spain). The methodology is based on the evaluation of the effects of main development actions on the habitat requirements of species. From these evaluations, and from data on the current distribution and population size (number of individuals) of each species, we estimated the most likely pattern of distribution and population size after the full implementation of the plans for each species. The impacts of the plans were quantified as the differences between the pre- and postproject patterns after codifying them to compensate for differences in the quality of the information available among species. Overall, we conclude that the proposed methodology fulfills the requirements for its use within the SEA process as it allows for the assessment of cumulative impacts on every species, highlighting the development directions and the habitat types with major impacts, and ascertaining whether impacts affect species with either low or high conservation and/or economic value. Generalization of the proposed methodology to other regions or species will require wildlife-habitat models adequate for SEA analyses, so that we also propose guidelines for the development and validation of these models.