我国农业废弃物资源化利用的激励机制研究

在激励机制缺失的情况下,我国农业废弃物资源化利用进展并不顺利。本文在考察梳理国外经验和我国废弃物利用现状和方向的基础上,借鉴管理激励理论,深入分析了当前我国农业废弃物资源化利用激励机制所面临的困境,从经济、技术、文化3个维度探讨了构建农业废弃物资源化利用激励机制的策略,并提出了促进农业废弃物资源化利用的具体政策措施。     

农业废弃物处理技术的分析

农业废弃物的资源化利用是节能减排和实现可持续发展的重要途径。本文首先分析了农业废弃物处理现状与存在问题,介绍了目前的能源化、肥料化、饲料化、材料化、基质化和生态化等利用方式;其次,分别介绍了秸秆、畜禽粪便、农村垃圾、农村污水4种主要农业废弃物的常用处理技术,同时对各项技术的应用特点、发展难点和发展前景进行了分析;最后,提出了农业废弃物处理的分类利用模式,提出了加快发展农业废弃物处理的政策建议。     

电子废弃物再生利用产业化的问题与对策研究

分析了目前我国电子废弃物再生利用产业化过程中存在的主要问题,提出了相关的对策和措施,并结合电子废弃物的特点提出了电子废弃物处理路线的设想。     

现代农作物废弃物的生态效应及资源化利用

通过分析我国农业废弃物对生态环境的影响以及农业废弃物资源化开发的现状,阐述了农业废弃物资源化开发利用存在的问题。提出生物技术、绿色工艺及开发节能环保建材等无害处理农业废弃物新途径,指出发展循环农业的有效模式,即建立生态农业多途径循环开发模式,植物、动物和微生物资源组成的“三维结构”的绿色新型农业,建立和推广生态型家庭经济模式,为推进农产品高效流通,促进农产品深度综合开发提供借鉴。     

国外电子废弃物的回收利用技术

本文介绍了国外电子废弃物（WEEE）的回收利用情况，着重介绍了电子废弃物中金属的回收技术，为国内电子废弃物的回收处理提供了一定的借鉴和参考。     

农业废弃物资源化利用技术现状及其前景

随着农业生产水平和农民生活水平的提高，对原来用作燃料和肥料的农业废弃物的利用越来越少，因此农业废弃物越来越多。本文综述了近年来国内外综合利用农业植物纤维性废弃物及畜禽粪便等农业废弃物的技术及有关研究进展情况，对农业废弃物的资源化综合利用方式进行了有益的探讨。     

浅谈电子废物变废为宝的绿色途径

电子废弃物已成为城市环境的新压力。本文从加强立法、生产者负责制以及建立健康绿色的废旧电子回收体系三方面分析电子废物变废为宝的绿色途径,从而推动电子废物资源化、无害化发展。     

国外电子废弃物的环境管理技术初探

电子工业的飞速发展带来了电子废弃物的问题。本文从电子废弃物的环境管理和处理处置技术的角度,概述了国外一些发达国家在电子废弃物处理方面的现状,并结合国外的发展经验,对我国环保产业的发展以及如何将电子废弃物的处理工作引向深入,提出了自己的设想和建议。     

德国电子废弃物循环利用体系的调查与思考

德国主要电子废弃物冰箱、显像管和灯管的循环利用技术和体系以及现行的法律法规，对我国电子废弃物的循环利用具有借鉴意义，因而应尽快建立生活垃圾和电子废弃物分类收集体系，充分利用可回收资源。     

我国电子废弃物处理产业现状与前景探讨

电子废弃物处理产业是伴随我国近年来社会经济快速发展而产生的一个新兴产业。本文分析了电子废弃物的经济价值、处理技术和产业政策,并对我国电子废弃物处理产业的现状与前景进行了探讨。     

废旧电子电气设备回收处理的研究进展

概述了目前全球对废旧电子电气设备(Waste of Electronic Electric Equipment,简称WEEE)回收处理的基本情况,并根据废旧电子电气设备处理的特点,从机械物理处理方法、热化学处理方法以及处理过程中产生有毒有害物质的分离技术三方面,介绍近年来废旧电子电气设备回收处理的研究进展,最后指出了真空热解的使用将作为未来废旧电子电气设备处理的发展方向。     

Present status of the recycling of waste electrical and electronic equipment in Korea

In Korea due to rapid economical growth followed by urbanisation, breakage of large traditional families into small nuclear families, continuous changes in equipment features and capabilities causes tremendous increase in sale of new electrical and electronic equipment (EEE) and decrease in sale of used EEE. Subsequently, the ever-increasing quantity of waste electrical and electronic equipment (WEEE) has become a serious social problem and threat to the environment. Therefore, the gradual increase in the generation of WEEE intensifies the interest for recycling to conserve the resources and protect the environment. In view of the above, a review has been made related to the present status of the recycling of waste electrical and electronic equipment in Korea. This paper describes the present status of generation and recycling of waste electrical and electronic equipment, namely TVs, refrigerators, washing machines, air conditioners, personal computers and mobile phones in Korea. The commercial processes and the status of developing new technologies for the recycling of metallic values from waste printed circuit boards (PCBs) is also described briefly. Since 1998, three recycling centers are in full operation to recycle WEEE such as refrigerators, washing machines and air conditioners, having the total capacity of 880,000 units/year. All waste TVs are recently recycled on commission basis by several private recycling plants. The recycling of waste personal computers and mobile phones is insignificant in comparison with the amount of estimated obsolete those. Korea has adopted and enforced the extended producer responsibility (EPR) system. Korea is making consistent efforts to improve the recycling rate to the standards indicated in the EU directives for WEEE. Especially environmentally friendly and energy-saving technologies are being developed to recycle metal values from PCBs of WEEE.     

Implementation of Waste Electrical and Electronic Equipment Directive in Finland: Evaluation of the collection network and challenges of the effective WEEE management

Further to the European Waste Electrical and Electronic Equipment (WEEE) Directive, setting up efficient collection schemes is necessary to ensure the recovery targets set. Following the subsidiary principle, the WEEE Directive defines only the general requirements for mandatory collection and recycling objectives. The modalities of the logistics and the organisation of the take-back schemes are left to the choice of Member States. In this paper, the implementation of the WEEE Directive and the development of the WEEE recovery infrastructure in Finland are described and the challenges to the effective management of the WEEE recovery system in Finland are expressed. It can be said that the implementation of the WEEE Directive has succeeded in Finland and, at the same time, the legislative basis has been enacted. In addition, a functional WEEE recovery infrastructure has been built and, the collection requirements of the WEEE Directive have been exceeded in a relatively short time. However, the paper outlines that some inefficient practices still exist, particularly in the registration and WEEE collection stages. It is concluded that raising awareness would lead to a more environmentally sound behaviour and would, ultimately, improve WEEE recovery efficiency.     

EPR在电子废物管理中的应用

指出电子废物具有商品性、外部性、公共物品三个经济学属性,以及在市场条件下上述属性所带来的市场失灵问题。研究了延伸生产者责任的理念、框架和种类,总结了电子废物延伸生产者责任制度的两种执行方式。借鉴国外先进经验、针对我国实际现状,提出了分阶段完善我国电子废物管理体制的政策建议。     

德国双元系统对电子废弃物回收的启示

本文回顾了德国双元系统在包装物回收领域取得的成功，探讨了此系统应用于电子废弃物回收的可行性与优势。针对电子废弃物的特性，本文提出了一系列相应的改进措施，使德国双元系统能够适用于电子废弃物的回收。     

Determination of toxic metals in discarded Liquid Crystal Displays (LCDs)

This study focused on the determination of the toxic metal content of Liquid Crystal Displays (LCDs) present in various Waste Electrical and Electronic Equipment (WEEE). The main objective was the identification and quantification of toxic metals detected in LCD panels. An experimental procedure which involved dismantling, shredding, pulverization, digestion and chemical analysis was followed for the sorting, separation and analysis of LCD monitors from various electronic devices that are currently on the market. Nine selected devices were examined, originated from four different types of e-waste (WEEE); TVs, computers, mobile phones and tablets. Eleven metals were measured in all examined samples. In addition, concentration values of chromium (Cr), cadmium (Cd), lead (Pb) and mercury (Hg) were compared with the respective limits set by the RoHS 2002/95/EC Directive that was recently renewed by the 2012/19/EU recast. The comparison revealed that the examined toxic metals on LCD panels did not exceed the limits set by the European Union (EU). Furthermore, when results were compared to the TTLC regulatory limits it was revealed that in three samples As concentrations were higher than the limit. Finally, when the TCLP test was implemented the aforementioned samples did not exhibit proportionally elevated values in their leachates.     

Sound management of brominated flame retarded (BFR) plastics from electronic wastes: State of the art and options in Nigeria

Management of flame retarded plastics from waste electrical and electronic equipment (WEEE) has been posing a major challenge to waste management experts because of the potential environmental contamination issues especially the formation of polybrominated-dioxins and -furans (PBDD/F) during processing. In Nigeria, large quantities of electronic waste (e-waste) are currently being managed—a significant quantity of which is imported illegally as secondhand electronics. As much as 75% of these illegal imports are never reused but are rather discarded. These waste electronic devices are mostly older equipment that contains brominated flame retardants (BFRs) such as penta-brominated diphenyl ethers (PBDEs), and polybrominated biphenyls (PBBs) which are presently banned in Europe under the EU WEEE and RoHS Directives. Risk assessment studies found both to be persistent, bio-accumulative and toxic. The present management practices for waste plastics from WEEE in Nigeria, such as open burning and disposal at open dumps, creates potential for serious environmental pollution. This paper reviews the options in the environmentally sound management of waste plastics from electronic wastes. Options available include mechanical recycling, reprocessing into chemicals (chemical feedstock recycling) and energy recovery. The Creasolv^® and Centrevap^® processes, which are the outcome of the extensive research at achieving sound management of waste plastics from WEEE in Europe, are also reviewed. These are solvent-based methods of removing BFRs and they presently offer the best commercial and environmental option in the sound management of waste BFR-containing plastics. Because these developments have not been commercialized, WEEE and WEEE plastics are still being exported to developing countries. The industrial application of these processes and the development of eco-friendlier alternative flame retardants will help assure sound management of WEEE plastics.     

生产者责任延伸制度在电子废弃物管理中的探讨

电子废弃物的污染问题日益引起人们的关注，而我国传统废弃物的处理和管理制度的不完善使大量的有用资源没有得到有效回收，不符合全民节约和循环经济原则。本文从环境经济学角度，结合其它国家和地区的生产者责任延伸制的颁布和运行情况，对我国电子废弃物的管理中施行生产责任延伸制（EPR）进行初步探讨。     

Environmental impacts and use of brominated flame retardants in electrical and electronic equipment

Management of waste electrical and electronic equipment (WEEE) or e-waste is becoming a major issue as around 20–50 million tons of such waste is generated worldwide and increasing at a higher rate than other solid waste streams. Electrical and electronic equipment (EEE) contains over 1,000 materials of which brominated flame retardants (BFRs) such as polybrominated biphenyls (PBBs) and polybrominated diphenyl ethers (PBDEs) have been the target of the regulators forcing manufacturers to adopt halogen-free flame retardants. As far as these alternatives are concerned, key consideration should be its performance during the whole life cycle through design, use and end-of-life management. The global halogen-free flame retardant movement has reached a point of no return. The most important issue as far as the environment is concerned, for which the transformation to halogen-free retardants was initially targeted, is to make sure that life span of the EEE using the alternatives to BFRs is not shortened thereby resulting in unforeseen increases in e-waste to deal with. The aim of this article is to investigate the environmental issues and current developments related to the use of BFRs in EEE manufacture. It describes the sources, toxicity and human exposure of BFRs, EOL management such as recycling and thermal treatments, exposure of BFRs from e-waste processing facilities and the environment around them and examines the developments and feasibility of the alternatives to BFR in EEE manufacture.