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21.
高浓印染废水处理工程的设计审计与运行结果分析 总被引:3,自引:1,他引:3
通过对漂染厂生产工艺过程及排废状况进行审计研究,提出了有针对性的废水处理工艺流程,区别对待废水浓度、污染物成分、化学作用及其工艺原理,实现了废水处理各工艺段的适配与综合节能的协调,在保证废水高效达标处理的前提下使工程优化 相似文献
22.
白宇辰 《安全.健康和环境》2020,(1):16-21
为保证乙烯装置的长期稳定运行,通过本质安全的设计和合理化操作,主要从高压脱丙烷塔、碳二前加氢、前冷系统、脱乙烷塔、甲烷化、乙烯精馏塔、丙烯精馏塔、脱丁烷塔等方面对乙烯装置可能出现的偏离正常操作情况做了详细的阐述,具有一定的指导意义。 相似文献
23.
Proost Stef Van Regemorter Denise 《Mitigation and Adaptation Strategies for Global Change》2004,9(4):453-473
In this paper we discuss the effects ofdifferent climate change policies onindustrial activity and on welfare. Wecompare the effects of carbon taxes andgrandfathered permits and the effects ofexemptions for energy-intensive industries.We survey first the insights from economictheory and from model experiments for theUS. Next we use a general equilibrium modelto assess the effect of different climatechange policies on industrial activity persector and per member country in the EU. Wepay particular attention to the effects ofpolicies where one EU member state exemptsits energy-intensive sectors from abatementefforts. The main findings are that, in theEU, the effects on industrial activity andthe welfare costs of tradable permits orcarbon taxes are small when no industrialsectors are exempted. When one membercountry exempts its energy intensivesector, this will reduce somewhat theimpact on its activity level but willgenerate an extra welfare cost for theEU. 相似文献
24.
生物接触氧化法处理煤矿生活污水的工艺探讨 总被引:2,自引:0,他引:2
根据煤矿生活污水的特点,结合几年来工作和学习的经验及体会,论述生物接触氧化法的工艺流程,讨论设计中遇到的问题,探讨设计参数,使用填料和选取方法,为今后的污水处理站设计提供参考。 相似文献
25.
目的 研究GJB 150.8A—2009《军用装备实验室环境试验方法第8部分:淋雨试验》中强化试验程序的工程实现方法.方法 在标准解读的基础上,以强化试验程序用喷嘴为对象,建立数值模型,分析喷嘴在强化试验程序过程中的流场分布,并基于分析结果给出强化试验程序试验装置设计的思路和方法.结果 在喷嘴内,压力变化剧烈,极短距离内由276 kPa迅速降至101 kPa.水流经过喷嘴经历了激烈的加速过程,从距离喷嘴出口0.01~0.4 m,水流速度从251 m/s迅速降至17.8 m/s,到远场趋于稳定.结论 分析结果对指导强化试验程序的试验装置的设计和试验实施具有重要参考意义. 相似文献
26.
This paper explores the practical application of life cycle assessment (LCA) to product system development. While life cycle assessment methods have been studied and demonstrated extensively over the last two decades, their application to product design and development has not been critically addressed. Many organizational and operational factors limit the integration of the three LCA components (inventory analysis, impact assessment and improvement assessment) with product development. Design of the product system can be considered a synthesis of individual decisions and choices made by the design team, which ultimately shape the system's environmental profile. The environmental goal of life cycle design is to minimize the aggregate environmental impacts associated with the product system. Appropriate environmental information must be supplied to decision makers throughout each stage of the development process to achieve this goal. LCA can serve as a source of this information, but informational requirements can vary as the design moves from its conceptual phase, where many design choices are possible, to its detailed design and implementation. Streamlined approaches and other tools, such as design checklists, are essential. The practical use of this tool in product development also depends on the nature and complexity of the product system (e.g. new vs. established), the product development cycle (time-to-market constraints), availability of technical and financial resources, and the design approach (integrated vs. serial). These factors will influence the role and scope of LCA in product development. Effective communication and evaluation of environmental information and the integration of this information with cost, performance, cultural and legal criteria will also be critical to the success of design initiatives based on the life cycle framework. An overview of several of these design initiatives will be presented. 相似文献
27.
Torvanger Asbjørn Rypdal Kristin Kallbekken Steffen 《Mitigation and Adaptation Strategies for Global Change》2005,10(4):693-715
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. 相似文献
28.
29.
面向回收的产品设计能够使废旧产品得到更好的回收和重用,优化拆卸序列的生成必须基于产品拆卸的经济性分析。论述了面向经济回收的产品设计系统的构成及相关的关键问题,分析了产品的零件材料回收价值与拆卸工艺,建立了零件材料合理回收的评估方法。 相似文献
30.