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11.
1 IntroductionMercury(Hg)asaglobalpollutanthascausedconcernworldwidesincetheendof 1980s.Itisemittedtotheatmospherefrombothanthropogenicandnaturalsources.Importantsourceoftheformeristhedischargefrom productionanduseofHgaswellasthecombustionoffossilfuels(Nri…  相似文献   
12.
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   
13.
烟气脱硫副产物的综合利用   总被引:4,自引:0,他引:4  
本文通过分析烟气脱硫石膏的性能,介绍了脱硫石膏的利用情况和研究进展,利用脱硫石膏生产建筑材料,如建筑石膏和高强石膏的工艺越来越成熟,利用脱硫石膏生产水泥辅料已进入工业化,而利用脱硫石膏生产充填尾砂胶结剂已经完成试验阶段,利用脱硫石膏生产路基回填材料,脱硫石膏在农业上也有广泛的用途。  相似文献   
14.
利用生命周期评价工具对企业的生产过程进行全面分析与评价,做好企业清洁生产的审核工作具有重要理论研究价值和现实应用意义。运用生命周期评价方法对重庆小南海水泥厂普通硅酸盐水泥生产过程进行了初步评价,认识了普通硅酸盐水泥生产过程的环境协调性,为普通硅酸盐水泥进一步提高环境性能提供了理论依据。  相似文献   
15.
本文简述了乌兰水泥有限责任公司在生产管理和生产过程中主动实施清洁生产的一些经验和成绩。即从项目建设初期就严格执行国家有关环保的法律法规,如“三同时”制度并将清洁生产的理念贯穿于管理和生产的始终,到污染治理方面选用有效的技术措施和管理手段等。简述了先进环保设施及科学管理手段是实现清洁生产的根本。  相似文献   
16.
降低油品储运损耗 改善大气环境   总被引:4,自引:0,他引:4  
从石油开采到成品油进入清费的过程中,损耗量约占原油量的3%-5%,其中储运过程中的损耗占总耗的40%-50%,着重论述了油品储运过程中降低损耗的措施,以减少经济损失和对环境的破坏。  相似文献   
17.
利用独特的设备和水泥窑的工艺特点,用废物代替水泥生产中的原材料,合理处置危险废物,使环境治理和循环经济达到有效的结合,是一项废物处理和资源化的新途径,是水泥生产企业可持续发展的方向之一,具有广阔的发展前景。  相似文献   
18.
对燕化公司开展环保全面达标工作做了综述和总结,几年的综合污染防治工作证明,加强环保管理、持续推行清洁生产和较先进的污染治理技术促进了燕化公司经济和生产的发展,同时降低了废物排放,取得了明显的效果。  相似文献   
19.
对搞好安全生产必须依靠安全科技进行了论述.提出了在安全工作中必须运用科技手段的必要性和必须正视的几个现实问题.  相似文献   
20.
The Lawrence Berkeley National Laboratory (Berkeley Lab) and the Center for Sustainable Development in the Americas (CSDA) conducted technical studies and organized two training workshops to develop capacity in Central America for the evaluation of climate change projects. This paper describes the results of two baseline case studies conducted for these workshops, one for the power sector and one for the cement industry, that were devised to illustrate certain approaches to baseline setting. Multiproject baseline emission rates (BERs) for the main Guatemalan electricity grid were calculated from 2001 data. In recent years, the Guatemalan power sector has experienced rapid growth; thus, a sufficient number of new plants have been built to estimate viable BERs. We found that BERs for baseload plants offsetting additional baseload capacity ranged from 0.702 kgCO2/kWh (using a weighted average stringency) to 0.507 kgCO2/kWh (using a 10th percentile stringency), while the baseline for plants offsetting load-following capacity is lower at 0.567 kgCO2/kWh. For power displaced from existing load-following plants, the rate is higher, 0.735 kgCO2/kWh, as a result of the age of some plants used for meeting peak loads and the infrequency of their use. The approved consolidated methodology for the Clean Development Mechanism yields a single rate of 0.753 kgCO2/kWh. Due to the relatively small number of cement plants in the region and the regional nature of the cement market, all of Central America was chosen as the geographic boundary for setting cement industry BERs. Unfortunately, actual operations and output data were unobtainable for most of the plants in the region, and many data were estimated. Cement industry BERs ranged from 205 kgCO2 to 225 kgCO2 per metric ton of cement.  相似文献   
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