MSW好氧生物反应器与单纯好氧填埋的对比实验

设计了一组对比实验 ,即城市固体废物 (MSW)好氧生物反应器与单纯好氧填埋方式的对比实验。其中MSW好氧生物反应器是强制通风好氧填埋和渗滤液循环两种填埋方式有机结合体。通过该对比实验研究两者对填埋的垃圾及所产生的渗滤液的降解情况 ,从而得出MSW好氧生物反应器有很好的降解效果     

硫化碱脱除二氧化硫工业烟气的可行性分析

分析了国内外烟气脱硫的研究现状,论述了用硫化碱脱除二氧化硫化工业烟气在理论上和实验上的可能性。     

皮革废物铬革屑的微生物学处理研究Ⅱ:降解革屑微生物的发酵条件及其蛋白酶的降解研究

在以皮胶原为碳、氮源时其最适产酶条件为ｐ Ｈ７ ,３０ ℃,高产酶时间为４ ｄ ．经 Ｃａ（ Ｏ Ｈ）２ 预处理革屑不能有效促进该菌对革屑的降解,但可使大部分 Ｃｒ３ ＋ 沉淀而除去．经该株蛋白酶的粗提及性质实验,确定酶的最适反应条件为４０ Ｃ、ｐ Ｈ７ ．０ ～８ ．０ , Ｃｒ３ ＋ 对酶有轻度的抑制作用,以２ ．２６ ％ 的粗酶作用于革屑,水解率达５０ ％ 以上     

用聚苯乙烯泡沫塑料废弃物调制油性腻子

以工业废弃物聚苯乙烯泡沫塑料及电厂粉煤灰为主要原料,用适量轻溶剂油调制成油性腻子,搅拌均匀经三辊机或轮碾机研磨至完全均匀细腻,包装即得产品。该产品的性能与同类油性腻子相似,而制造成本显著降低,适用于填平金属、木质、混凝土物体表面的凹坑、针孔和缝隙,同时减少了白色污染物聚苯乙烯泡沫塑料废弃物对环境的污染。     

Methodological aspects of life cycle assessment of integrated solid waste management systems

Environmental life cycle assessment (LCA) developed rapidly during the 1990s and has reached a certain level of harmonisation and standardisation. LCA has mainly been developed for analysing material products, but can also be applied to services, e.g. treatment of a particular amount of solid waste. This paper discusses some methodological issues which come into focus when LCAs are applied to solid waste management systems. The following five issues are discussed. (1) Upstream and downstream system boundaries: where is the ‘cradle’ and where is the ‘grave’ in the analysed system? (2) Open-loop recycling allocation: besides taking care of a certain amount of solid waste, many treatment processes also provide additional functions, e.g. energy or materials which are recycled into other products. Two important questions which arise are if an allocation between the different functions should be made (and if so how), or if system boundaries should be expanded to include several functions. (3) Multi-input allocation: in waste treatment processes, different materials and products are usually mixed. In many applications there is a need to allocate environmental interventions from the treatment processes to the different input materials. The question is how this should be done. (4) Time: emissions from landfills will continue for a long time. An important issue to resolve is the length of time emissions from the landfill should be considered. (5) Life cycle impact assessment: are there any aspects of solid waste systems (e.g. the time horizon) that may require specific attention for the impact assessment element of an LCA? Although the discussion centres around LCA it is expected that many of these issues are also relevant for other types of systems analyses.     

实施污水总量控制的经验和做法

为实现２０００年达标排放和总量控制目标,胜利油田的经验和做法是：制定了污水排放总量控制计划、总量控制监测及监督考核办法;认真搞好工业污水治理和综合利用,重点抓好采油污水的回注,使回注率大于９０％,并对各行业污水治理制定了措施     

油田采油注入水处理技术

介绍了中原油田注入水水质特点,以前采用的处理工艺和存在的问题,并分析了问题的根源在于产出水的“四高一低”,原处理工艺难以去除。针对这一情况,中原油田与江汉石油学院合作开发研制了三组分水质调整剂,分别调整ｐＨ,破坏液体的稳定性并去除液体中的金属离子;他们对三种组分的加入时间和投加量进行了试验,结果表明：三种组分应按顺序加入,其中Ａ、Ｂ剂应有足够的间隔,加入量根据不同水质由试验确定。通过中原油田水处理站的运行试验得出结论：该工艺简单,投资小,处理效果好,适合中原油田的水质特性;处理后的水水质稳定,有效控制了腐蚀,减少了穿孔损失和污染损失,取得了显著的社会效益和环境效益     

A/O~2法在炼油污水处理中的应用

为探索Ａ／Ｏ２（厌氧Ａｎａｅｒｏｂｉｃ／好氧Ｏｘｉｃ／好氧Ｏｘｉｃ）法在处理炼油污水中的应用,进行了Ａ／Ｏ２法中型试验,验证ＮＨ３－Ｎ容积负荷与去除率之间的关系,以及溶解氧、含油量对处理效果的影响等几项内容。Ａ／Ｏ２法应用于炼油污水的处理是可行的,对ＣＯＤ、ＮＨ３－Ｎ、油、酚、ＳＳ等有很好的处理效果。将Ａ／Ｏ２法应用于济南炼油厂,各构筑物运转正常,处理效果很好,完全达到国家排放标准。Ａ／Ｏ２用来处理炼油污水,工艺可行、技术先进、经济合理,不仅对ＣＯＤ、氨氮去除率高,对其它排放指标去除率都很高。实践证明Ａ／Ｏ２法用来处理炼油污水是完全可行的,济南炼厂污水处理的成功经验值得推广。     

INTEGRATING SOCIAL BENEFIT COST ACCOUNTING INTO WATERSHED RESTORATION AND PROTECTION PROGRAMS1

ABSTRACT: Successful watershed management requires consideration of multiple objectives and the efficient use of scarce public and private resources. One way to address these multi-faceted issues is through Social Benefit-Cost Accounting (SBCA). SBCA is a systematic method of addressing complex social and economic issues relevant to proposed watershed management projects. Benefits of using this technique include: benefits and costs of watershed projects are better understood; politically sensitive issues tend to be put into perspective; and stakeholders' interests are placed on a level playing field. An example from Bogota, Colombia demonstrates how SBCA can be used to value the benefits and costs of a proposed project. By addressing the benefits and costs to all stakeholders, the design of watershed management programs can be improved to achieve goals in a cost-effective manner.