城市电子废弃物资源化管理模式构想

通过对惠州市电子废弃物收集体系组成、去向以及电子废弃物处置方式的调查,分析惠州市电子废弃物收集和处置存在的一系列问题,结合实际提出了城市电子废弃物资源化管理模式的初步构想。     

我国电子废物污染现状及环保利用浅析

通过分析与电子废物回收处理密切联系的工艺技术、规划管理和各种外部环境等因素,剖析我国电子废物处理产业面临的障碍,并提出解决建议。     

提高电子元器件使用可靠性的方法

针对实际工作中元器件使用可靠性方面存在的问题．本文通过在实际工作的经验积累和技术研究总结，在电子元器件的选择与检测控制等方面，提出了提高电子元器件使用可靠性的方法。实践证明，这些方法可以直接应用于电子元器件的工程选择与检测控制。     

甲胺生产废水中氨氮资源化的试验研究

利用MgSO4·7H2O和Na2HPO4·12H2O作为试验药剂,通过正交试验和单因素优化试验,对化学沉淀法处理甲胺生产废水中氨氮的工艺条件进行优化.结果表明,在pH=9.4、反应时间15 min、搅拌速度150 r/min、Mg:N(摩尔比值)=1.1、P:N(摩尔比值)=1.0时,化学沉淀法处理300 mL甲胺生产废水,氨氮去除率维持在92%以上,COD去除率可达37%以上.同时为验证工艺条件适应性和沉淀物(MgNH4PO4)作为农作物肥料使用的价值性,对最优条件下得到的沉淀物进行研究.与MgNH4PO4纯度为100%相比,沉淀物MgNH4PO4纯度达到86%以上.因此,化学沉淀法处理氨氮不仅具有良好的效果,而且得到的MgNH4PO4含有较高N、P,可以用作农作物肥料.     

电子产品故障物理模型研究与应用进展

提出了故障物理模型的基本概念,对几种常见的电子产品故障物理模型,包括互连热疲劳模型、互连振动疲劳模型、电迁移模型和与时间相关的介质击穿模型等进行了分析,总结提出了基于失效发生因素和失效发生过程的损伤模型建模等两种故障物理模型的建模方法。结合工程应用情况,对两种故障物理模型的应用方法——可靠性仿真分析方法和可靠性加速试验方法进行了讨论。最后对故障物理模型的研究进行了展望。     

电子垃圾重金属污染及防治对策研究

随着信息产业的飞速发展,电子产品更新换代加速,电子垃圾飞速增长,电子垃圾中的重金属对环境造成了越来越严重的污染.本文回顾了广东贵屿与浙江台州两大电子垃圾回收拆解区重金属污染的现状,分析了电子产品原材料、加工工艺和电子垃圾不当回收导致重金属污染的原因,提出了依靠政策法规引导、借鉴国外先进经验、进行电子垃圾回收处理产业化发展的相应防治对策,以期能改善电子垃圾导致的重金属污染.     

工业自动化制造企业环境因素的识别和影响研究

企业通过建立ISO14001环境管理体系(EMS),即可以提升企业的社会形象,也能更好帮助企业实现其承担的社会责任.在实践中,明确组织的环境因素是建立符合、有效的EMS的基础,也是组织进行环境规划活动的首要步骤.本文将以某外商独资企业为例,基于该类高附价值产品的制造企业特点,建立了环境因素识别的输入输出模型来全面识别环境因素,并分析了其对企业带来的相关环境影响.最后本文讨论了企业的节能减排案例,以及相关方的环境因素的影响和管理.     

弹上电子部件加速因子估计方法研究

目的针对高可靠长寿命的弹上电子部件在实际贮存环境温度起伏变化的情况,研究基于等效温度的加速因子估计方法。方法首先剖析弹上电子部件失效机理,然后基于阿伦尼斯模型,分析加速应力与实际环境温度的对应关系,求解实际环境等效温度,进而估计加速因子,最后通过某型导弹综合控制器中的时序控制电路板,验证该方法的工程适用性。结果该方法能够真实反映环境温度情况,且与传统加权平均温度计算方法相比,加速因子估计和加速试验时间预测更准确,且随着实际环境温度起伏的增大,优势更加明显。结论该方法在实际贮存环境温度起伏变化的情况下,能够有效提高加速因子估计和加速寿命试验时间预测的准确性,为弹上电子部件加速寿命试验方案设计提供可靠依据,对其他高可靠长寿命产品的加速因子估计也具有一定的参考价值。     

Two decades,three WEEE systems: How far did EPR evolve in Korea's resource circulation policy?

Extended producer responsibility (EPR) has become a dominant policy paradigm for the management of waste electrical and electronic equipment (WEEE) in the last two decades. In South Korea the principle has guided the evolution of the resource circulation policy even before its official introduction through a revision of the recycling law in 2002. Elements of producer responsibilities could be found in the producer-based deposit refund system (DRS) a decade earlier and they were strengthened through the enactment of a new resource circulation law in 2008. This article reviews the policy changes in South Korea for the management of WEEE during the past 20 years. The focus of the analysis is on the impacts of EPR and the producers’ responses that were expressed through the quantity and the quality of material flows in the society. The findings are discussed in light of international experiences in order to outline measures to improve the effectiveness of the EPR-based resource circulation policy that could have broader implications beyond the case study.     

Environmental resource footprinting of drug manufacturing: Effects of scale-up and tablet dosage

The formulation and scale-up of batch processes is one of the major challenges in the development of pharmaceutical dosage forms and at the same time a significant resource demanding process which is generally overlooked in environmental sustainability assessments. First, this paper proposes general trends in the experience curve of cumulative resource consumption of pharmaceutical tablet manufacturing of PREZISTA^® 800 mg through wet granulation (WG) at four consecutive scales in both R&D and manufacturing environments (resp. WG1 = 1 kg/h, WG5 = 5 kg/h, WG30 = 30 kg/h and WG240 = 240 kg/h). Second, the authors aim at evaluating the environmental impact from a life cycle perspective of a daily consumption of PREZISTA^® 2× 400 mg tablets versus the bioequivalent PREZISTA^® 800 mg tablet which was launched to enhance patient compliance. Environmental sustainability assessment was conducted at three different system boundaries, which enables identification, localization and eventually reduction of burdens, in this case natural resource extraction. Exergy Analysis (EA) was used at process level (α) and plant level (β) while a cradle-to-gate Exergetic Life Cycle Assessment (ELCA) was conducted at the overall industrial level (γ) by means of the CEENE method (Cumulative Exergy Extraction from the Natural Environment). Life cycle stages taken into account are Active Pharmaceutical Ingredient (API) production, Drug Product (DP) production and Packaging. At process level (α), the total resource extraction for the manufacturing of one daily dose of PREZISTA^® (800 mg tablet) amounted up to 0.44 MJ_ex at the smallest scale (WG1) while this amount proved to be reduced by 58%, 79% and 83% at WG5, WG30 and WG240 respectively. Expanding the boundaries to the overall industrial level (γ) reveals that the main resource demand is at the production of the Active Pharmaceutical Ingredient (API), excipients, packaging materials and cleaning media used in DP production. At the largest scale (WG240) the use of cleaning media during DP production contributes considerably less to the total resource extraction. Overall, the effect of scale-up and learning on resource consumption during DP production showed to possess a power-law experience curve y = 2.40 * x^−0.57 when shifting from WG1 (smallest lab scale) to WG240 (industrial manufacturing). Tablet dosage (2× 400 mg versus 1× 800 mg) did not significantly affect the absolute environmental burden. However, the relative contribution of resource categories did change due to the different production technology. It could be concluded that in meeting social and economic demands by launching the PREZISTA^® 800 mg tablet, no trade-off in environmental burden occurred. On the long term, future research should strive to take into account R&D processes and all services related to pipeline activities taking place prior to market launch and eventually to allocate impacts to the final product.