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1

Cooper, Tim. "WEEE, WEEE, WEEE, WEEE, all the way home? An evaluation of proposed electrical and electronic waste legislation." European Environment 10, no. 3 (2000): 121–30. http://dx.doi.org/10.1002/1099-0976(200005/06)10:3<121::aid-eet226>3.0.co;2-n.

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2

Andrei, Elena Ramona, Andreea Gabriela Oporan, Paul Ghioca, Lorena Iancu, Madalina David, Rodica-Mariana Ion, Zina Vuluga, Bogdan Spurcaciu, and Ramona Marina Grigorescu. "Waste Electrical and Electronic Equipment Processing as Thermoplastic Composites." Proceedings 57, no. 1 (November 12, 2020): 58. http://dx.doi.org/10.3390/proceedings2020057058.

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3

Dalrymple, I., N. Wright, R. Kellner, N. Bains, K. Geraghty, M. Goosey, and L. Lightfoot. "An integrated approach to electronic waste (WEEE) recycling." Circuit World 33, no. 2 (May 22, 2007): 52–58. http://dx.doi.org/10.1108/03056120710750256.

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PurposeThis paper aims to present a review carried out under DEFRA‐funded project WRT208, describing: the composition of WEEE, current treatment technologies, emerging technologies and research.Design/methodology/approachThis paper summarises the output from the first part of the project. It provides information on the composition of WEEE and an extensive survey of technologies relevant to materials recycling from WEEE. A series of further papers will be published from this research project.FindingsWEEE has been identified as one of the fastest growing sources of waste in the EU, and is estimated to be increasing by 16‐28 per cent every five years. Within each sector a complex set of heterogeneous secondary wastes is created. Although treatment requirements are complicated, the sources from any one sector possess many common characteristics. However, there exist huge variations in the nature of electronic wastes between sectors, and treatment regimes appropriate for one cannot be readily transferred to another.Research limitations/implicationsA very large number of treatment technologies are available, both established and emerging, that singly and in combination could address the specific needs of each sector. However, no single set of treatment methods can be applied universally.Originality/valueThis paper is the first part of work leading to the development of technical strategies and methodologies for reprocessing WEEE into primary and secondary products, and where possible the recovery of higher added‐value components and materials.
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4

Deaves, M. "Taking the WEEE [EU waste electrical and electronic equipment directive]." Manufacturing Engineer 82, no. 6 (December 1, 2003): 38–41. http://dx.doi.org/10.1049/me:20030608.

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5

Shah Khan, Safdar, Suleman Aziz Lodhi, Faiza Akhtar, and Irshad Khokar. "Challenges of waste of electric and electronic equipment (WEEE)." Management of Environmental Quality: An International Journal 25, no. 2 (March 4, 2014): 166–85. http://dx.doi.org/10.1108/meq-12-2012-0077.

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Purpose – The purpose of this paper is to analyze the recent global situation on waste of electric and electronic equipment (WEEE) management and recommend policy directions for designing environmental strategies. Design/methodology/approach – Qualitative research approach is adopted to review studies on WEEE management in developed and developing countries. The focus is to critically consider the available options for its safe management. Findings – Approximately 40-50 million tons of WEEE is generated worldwide annually and most of it is dumped in the developing countries. WEEE is not a challenge to be faced by a single country as it has trans-boundary effects and ultimately the contamination reaches back to the developed countries with a lapse of time. Research limitations/implications – Data availability on WEEE generation and disposal is in initial stages. Practical implications – Developing countries in Asia and Africa do not have resources to handle WEEE. The unregulated and unsafe WEEE management practices in these countries let hazardous materials to disseminate into the marine life and global ecosystem. Originality/value – The paper recommends policy directions to deal with the emerging issue that may have globally far reaching consequences.
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6

Tsai, Wen-Tien. "Recycling Waste Electrical and Electronic Equipment (WEEE) and the Management of Its Toxic Substances in Taiwan—A Case Study." Toxics 8, no. 3 (July 7, 2020): 48. http://dx.doi.org/10.3390/toxics8030048.

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In the past two decades, the waste electrical and electronic equipment (WEEE) management has become an important environmental issue internationally because it contained hazardous substances like heavy metals and brominated flame retardants. Moreover, some valuable substances were used in the electrical and electronic products, thus representing a circular industry for recycling of WEEE. Therefore, the Taiwan government formulated a legal WEEE recycling system since 1998 in response to the international trends of sustainable waste management and extended producer responsibility (EPR). This article adopted the national statistics in Taiwan regarding the online reporting amounts of collected WEEE since it has been officially designated as one of the mandatory recyclable wastes. Furthermore, the regulatory measures were addressed to update the status and subsidiary fee rates of WEEE recycling in Taiwan. In addition, this article also put emphasis on the regulations governing the toxic chemical substances contained in the WEEE. It showed that the average annual recycling amounts of home electronic appliances, information technology products and lighting in Taiwan during the 2017–2018 were around 117,000, 18,000 and 4500 metric tons, respectively. It was also indicated that the current WEEE recycling market in Taiwan has become saturated, reflecting the regulatory promulgation and promotional measures successfully. In response to the Stockholm Convention on persistent organic pollutants (POPs) and the Minamata Convention on Mercury, the Taiwan government declared some brominated flame retardants and heavy metals (i.e., mercury and cadmium) as a “toxic chemical substance” under the Toxic and Concerned Chemical Substance Control Act (TCCSCA), which shall be prohibited to use in the preparation of electrical and electronic equipment (EEE) since 1 January 2016. Through the central governing authority, local governments, and private recyclers in Taiwan, the successful WEEE recycling system not only reduce the pressure on sanitary disposal systems, but also prevent the chemical hazards from solid waste incineration systems. More significantly, the WEEE recycling in Taiwan echoed the United Nations (UN) Agenda 2030 for sustainable development goals.
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7

Andersen, Terje, Bjørn Jæger, and Alok Mishra. "Circularity in Waste Electrical and Electronic Equipment (WEEE) Directive. Comparison of a Manufacturer’s Danish and Norwegian Operations." Sustainability 12, no. 13 (June 28, 2020): 5236. http://dx.doi.org/10.3390/su12135236.

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Waste electrical and electronic equipment (WEEE) as a reverse supply chain (RSC) has a low degree of circularity, mainly focusing on recovering or recycling. Targets to increase the circularity have recently been introduced in the EU WEEE directive. In this case study, we have investigated how WEEE is handled within an electric and electronic (EE) equipment manufacturer. The case study includes findings from two different Nordic countries, Norway and Denmark, with interviews of six stakeholders. The case study shows that there are significant differences in how the case company fulfills its extended producer responsibility (EPR), especially related to reporting. The study also found that there is a mismatch between the ambitions in the WEEE directive and a company’s approach related to circularity in the end-of-life phase of an EE product. Based on the results of this case study and from the literature we propose recommendations on alignment with other directives and on a common information regime within the WEEE RSC.
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8

Fayustov, A. A., and P. M. Gureev. "Electrical and Electronic Equipment Waste Management Problems." Ecology and Industry of Russia 24, no. 6 (June 17, 2020): 60–66. http://dx.doi.org/10.18412/1816-0395-2020-6-60-66.

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The article discusses the consequences of the development of the economy, processes and services, expressed in a sharp increase in the number of operating electronic equipment, which directly leads to an increase in the generated volumes of waste electrical and electronic equipment (WEEE) and the problems of their disposal. Various types of electronic equipment containing substances that constitute a serious threat to the ecology and human health, especially with improper disposal, are analyzed. The existing foreign and domestic experience in the field of electronic waste disposal is considered. The system of recycling electronic waste adopted in the EU countries and regulatory documents operating abroad and in the Russian Federation was studied. Practical recommendations are proposed for creating a real WEEE management system taking into account the actual situation in Russia and world experience in this area.
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9

Gurauskiene, Inga, and Zaneta Stasiskiene. "MODEL FOR REGIONAL MANAGEMENT OF ELECTRICAL AND ELECTRONIC WASTE (WEEE) FLOWS." Environmental Engineering and Management Journal 17, no. 1 (2018): 135–45. http://dx.doi.org/10.30638/eemj.2018.015.

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10

Churchman-Davies, J. "Just a WEEE problem [waste management]." IEE Review 48, no. 6 (November 1, 2002): 38–40. http://dx.doi.org/10.1049/ir:20020605.

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11

Li, Jia Xiang, Chuan Huang, Yin Zhu, and Shan Huang. "WEEE Management in Chongqing, China: Status and Strategies." Advanced Materials Research 414 (December 2011): 39–44. http://dx.doi.org/10.4028/www.scientific.net/amr.414.39.

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This paper presents an examination of the current possession of electrical and electronic equipment (EEE) and predicted amount of waste electrical and electronic equipment (WEEE) in Chongqing. The results indicate that: the total EEE possession amount has reached a total of 287.73 million units in 2009; and the overall evaluated generation of WEEE from 2011 to 2015 would reach 13.53 million units, of which 19% are personal computers, 24% air conditioners, 7% refrigerators, 38% color TVs, and 12% washing machines, respectively. The recycling capacity is also investigated, evincing that about 952,000 waste units were recycled in 2009. There are three officially approved corporations for dismantling WEEE in 2010, with the dismantling capacity of 1,600,000 units per year. Moreover, several disposal facilities have been under construction and expect to be accomplished in 2015. This paper also proposes a number of recommendations aiming to improve the WEEE management system. For better management, it is necessary to arouse the public recognition of the need for formal processing of WEEE as well as to implement EPR approach, license system, and deposit-refund system.
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12

Pandey, Dr Shakuntala. "ELECTRICAL AND ELECTRONIC WASTE: A GROWING ISSUE." International Journal of Engineering Technologies and Management Research 4, no. 12 (April 24, 2020): 85–88. http://dx.doi.org/10.29121/ijetmr.v4.i12.2017.596.

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“WEEE” or Waste electrical and electronic equipments” A computer complete with monitor, keyboard, mouse and the central processing unit weight about 32 kg. But with no scientific system of recycling in place they are dumped as E-waste. Pile after pile of chips and assorted bits and pieces of computers are contributed by IT companies. As the IT segment tries to keep pace the recycling market gets flooded with fresh stocks of electronics materials - stripped, pounded and extracted. The BPO/IT segment is one of the largest generators of e-waste. As the problem of e-waste continues to grow bigger, the need to evolve clean means of disposal has become more urgent. Some private companies are working on scientific recycling of waste. The bulk of e-waste still travels to the scrap yards and the backroom recycler.
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13

Bahers, Jean-Baptiste, and Junbeum Kim. "Regional approach of waste electrical and electronic equipment (WEEE) management in France." Resources, Conservation and Recycling 129 (February 2018): 45–55. http://dx.doi.org/10.1016/j.resconrec.2017.10.016.

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14

Parajuly, Keshav, Komal Habib, and Gang Liu. "Waste electrical and electronic equipment (WEEE) in Denmark: Flows, quantities and management." Resources, Conservation and Recycling 123 (August 2017): 85–92. http://dx.doi.org/10.1016/j.resconrec.2016.08.004.

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15

Shad, Khalid Mehmood, Yen Ling Tan, and Mohammad Ershadul Karim. "SUSTAINABLE E-WASTE MANAGEMENT IN MALAYSIA: LESSONS FROM SELECTED COUNTRIES." IIUM Law Journal 28, no. 2 (December 28, 2020): 415–47. http://dx.doi.org/10.31436/iiumlj.v28i2.517.

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The seriousness of electrical and electronic equipment waste (E-waste/WEEE) problem is currently haunting both developed and developing nations around the world. WEEE in layman’s term can be defined as discarded components of electrical and electronic equipment that have no reuse value. Improper disposal of WEEE can bring about catastrophic effects to mankind and the environment. The Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal, 1992 categorises WEEE as hazardous waste due to the presence of toxic materials. Currently, the production of WEEE is expanding at a significant rate and is expected to touch 52.2 million Mt tonnes globally by 2021. The nations around the world have taken initiatives such as introducing new laws, regulations and policies. Malaysia is also similarly affected by the increasing volume of WEEE and it has been reported that its WEEE would reach an aggregate of 762.507 million units by 2020. In response, the Malaysian government has drafted a new regulation, the Environmental Quality (Household Scheduled Waste) Regulation, which is currently under review by the Attorney General’s Chambers. Using the library-based research methodology, this legal research aims to provide a comprehensive overview of WEEE management from a global as well as the Malaysian perspective. A brief discussion on the classification of e-waste and analysis of key initiatives taken worldwide is provided and examined. The article concludes with a recommendation for the necessary actions that can be adopted to enhance best WEEE management practices in Malaysia, to ensure the threat imposed by WEEE on mankind and the environment is curtailed.
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16

Grigorescu, Ramona Marina, Madalina Elena Grigore, Paul Ghioca, Lorena Iancu, Cristian-Andi Nicolae, Rodica-Mariana Ion, Sofia Teodorescu, and Elena Ramona Andrei. "Waste Electrical and Electronic Equipment Study regarding the plastic composition." Materiale Plastice 56, no. 1 (March 30, 2019): 77–81. http://dx.doi.org/10.37358/mp.19.1.5127.

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Waste electrical and electronic equipment (WEEE) generated in large amounts due to the development of IT and telecommunication industry is considered an important concern for environmental protection. The complex polymer composition of WEEE can be determined in order to consider a proper recycling process for polymeric materials. The aim of the study was to identify the constituent polymers by: density, burning test, solubility, Fourier Transform Infrared Spectroscopy (FTIR), Differential Scanning Calorimetry (DSC), thermo-gravimetric analysis (ATG). The research led to a majority of polystyrenic polymers, together with polyesters, polycarbonates and polyamides.
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17

Rodrigues, Jaqueline Terezinha Martins Corrêa, and Liane Werner. "Forecasting methods of generation of waste electrical and electronic equipment: a systematic review." Exacta 17, no. 3 (September 30, 2019): 173–90. http://dx.doi.org/10.5585/exactaep.v17n3.8301.

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In recent decades there have been a significant increase in the use of electronic equipment in homes, offices and industries. When these equipment are discarded after have been used they become Waste of Electric and Electronic Equipment (WEEE). To know how the forecasting of WEEE´s generation were made, it was necessary to carry out a systematic review. The search was done in 5 databases by using the key words "electronic waste" or "WEEE" or "e-waste" and "forecasting" and it was found 854 articles. After applying the inclusion and exclusion criteria 28 articles were reached. As a result, it is noted that the selected articles are concentrated in the USA and China and in a few newspapers. The most independent variable used was the dada about the commercialization of the equipment. The majority of the articles have as variable response the unit and weight. There was also strong use of statistical tools and forecasting methods, especially the regression and the MFA (Material Flow Analysis).
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18

Kachmar, N., O. Mazurak, A. Dydiv, and T. Bahday. "Experience of certain countries in electronic and electric waste management." Scientific Messenger of LNU of Veterinary Medicine and Biotechnologies 21, no. 90 (April 26, 2019): 59–62. http://dx.doi.org/10.32718/nvlvet-a9010.

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The paper present result of research concerning the problems of handling electronic and electrical waste that households produce at home and analysed the main problems associated with this issue in Ukraine and in the world. The object of the study was telephones (ukrainians use 53.6 million mobile communication devices), refrigerators, washing machines and TVs. The production of electrical and electronic equipment is one of the fastest growing global manufacturing activities. This development has resulted in an increase of waste electric and electronic equipment which constitute a risk to the environment and sustainable economic growth. Recycling of electronic and electrical waste is very expensive. There is a problem with electronic and electrical waste in Ukraine. To accumulate in the soil or to burn these waste is harmful. Every year on our planet about 50 million tons of electronic waste are generated. It was established that 53% of the interviewed students changed 1 phone in the last three years, 24% – 2 phones and 7% – more than 3. Students wanted a new phone. Most of the phones are at home, and the rest were given to their relatives or thrown into the trash. Ukrainians replace refrigerators, TVs and washing machines less often. Most Ukrainians change refrigerators. The largest amount of electronic waste is produced in Australia, New Zealand and Oceania (17.3 kg per inhabitant), in Europe – 16.6 kg per inhabitant and 11.6 kg waste per inhabitant of North and South America. In Japan, Norway, the Netherlands, Germany, Sweden and Poland, the process of disposal of used home appliances is well organized. However, economically developed countries utilize only part of the waste in their territory, while the rest are exported to landfills in Pakistan, Vietnam, Nigeria. The world's largest dump of electronic and electrical waste is in Ghana. To address potential environmental problems that could stem from improper management of WEEE, many countries and organizations have drafted national legislation to improve the reuse, recycling and other forms of material recovery from WEEE to reduce the amount and types of materials disposed in landfills.
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19

Goodship, V., R. L. Cain, N. Reynolds, and M. W. Pharaoh. "The WEEE Directive: Information and Opportunities for Plastics Recycling." Progress in Rubber, Plastics and Recycling Technology 18, no. 3 (August 2002): 161–72. http://dx.doi.org/10.1177/147776060201800302.

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The forthcoming EU directive on Waste Electronic and Electrical Equipment will have far reaching effects throughout the plastics supply chain. Important factors are discussed such as the directives scope and policing, design and disassembly and potential market opportunities within and outside the existing supply chain.
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20

Dias, Pablo, Andréa Moura Bernardes, and Nazmul Huda. "Waste electrical and electronic equipment (WEEE) management: An analysis on the australian e-waste recycling scheme." Journal of Cleaner Production 197 (October 2018): 750–64. http://dx.doi.org/10.1016/j.jclepro.2018.06.161.

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21

Schlummer, Martin, Ludwig Gruber, Andreas Mäurer, Gerd Wolz, and Rudi van Eldik. "Characterisation of polymer fractions from waste electrical and electronic equipment (WEEE) and implications for waste management." Chemosphere 67, no. 9 (April 2007): 1866–76. http://dx.doi.org/10.1016/j.chemosphere.2006.05.077.

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22

Cetinsaya Özkır, Vildan. "Constructing small WEEE collection system in Istanbul: A decision support system and conceptual design proposal." An International Journal of Optimization and Control: Theories & Applications (IJOCTA) 7, no. 1 (October 12, 2016): 16–27. http://dx.doi.org/10.11121/ijocta.01.2017.00358.

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The technological advances decrease electrical/electronic product lifecycles and boost consumption of high-tech products. The rapid growth in the electronic market produces electronic waste streams and potential threats arise on sustainability in terms of depleting natural resources and improper disposal. End-of-life electrical/electronic equipment (EEEs) involves complex mixture of materials, has hazardous content, and if not properly disposed, they can cause major environmental and health problems. To prevent the consequences of improper disposal, authorities and researchers conduct large-scale projects aligned with European union legislations. However, these efforts are still not sufficient to establish effective and organized systems due to the problem complexity and the need for specialized arrangements. This study proposes conceptual decision support framework and a bi-objective mathematical model to construct an effective collection network for end-of-life mobile phones. A real case study is presented for constructing an effective collection system in Istanbul. The main reason that we select Istanbul, is the requirement of urgency to deal with the large quantities of e-wastes. The result of this study will encourage academicians to conduct further research studies and strongly assist the authorities to configure well-structured e-waste collection system.
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23

Martinho, Graça, Ana Pires, Luanha Saraiva, and Rita Ribeiro. "Composition of plastics from waste electrical and electronic equipment (WEEE) by direct sampling." Waste Management 32, no. 6 (June 2012): 1213–17. http://dx.doi.org/10.1016/j.wasman.2012.02.010.

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24

Alzate, Andrea, Maria Esperanza López, and Claudia Serna. "Recovery of gold from waste electrical and electronic equipment (WEEE) using ammonium persulfate." Waste Management 57 (November 2016): 113–20. http://dx.doi.org/10.1016/j.wasman.2016.01.043.

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25

Okorhi, O. J., E. E. Okereka, C. O. Akhimie, and K. K. Enekwenchi. "Frontiers and prospects for recycling Waste Electrical and Electronic Equipment (WEEE) in Nigeria." Journal of Applied Sciences and Environmental Management 21, no. 7 (February 16, 2018): 1382. http://dx.doi.org/10.4314/jasem.v21i7.30.

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26

Feszty, Katalin, Colin Murchison, Jim Baird, and Gholam Jamnejad. "Assessment of the quantities of Waste Electrical and Electronic Equipment (WEEE) in Scotland." Waste Management & Research 21, no. 3 (June 2003): 207–17. http://dx.doi.org/10.1177/0734242x0302100304.

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27

Jung, Insang, Jihwan Park, Jongsoo Hwang, and Wonhee Choi. "Overview and Recent Development of Recycling Small Waste Electrical and Electronic Equipment (WEEE)." Journal of the Korean Institute of Resources Recycling 24, no. 4 (August 31, 2015): 38–49. http://dx.doi.org/10.7844/kirr.2015.24.4.38.

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28

Asunción, Arner. "Extended Producer Responsibility for Waste Oil, E-Waste and End-of-Life Vehicles." International Journal of Economics and Financial Research, no. 610 (October 22, 2020): 222–35. http://dx.doi.org/10.32861/ijefr.610.222.235.

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This paper aims to explore the relationships of the performance of producer responsibility organizations (PROs) for waste oil, waste electrical and electronic equipment (WEEE), and end-of-life vehicles (ELV). The methodology consists in estimating the cointegration equations between the variables of lubricating oil production (SIG), electric and electronic equipment (EEE), and vehicle production (VP) using dynamic ordinary least squares (DOLS). Subsequently, elasticities are got based on estimates for Spain over the period 2007-2019 using quarterly data. The main results were that SIG and EEE were cointegrated variables. The elasticity of the SIG variable up to EEE was positive at 2, 4166. Additionally, the elasticity of the SIG variable up to VP was 2, 4050. However, SIG and VP are not cointegrated variables; subsequently, it was not a stable relationship between these variables. Results suggest it was because EPR was applied in WEEE PRO join with a deposit refund system (DRS); meanwhile, EPR in ELV PRO had been applied without subsidies to purchase cars.
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Widyarsana, I. Made Wahyu, Dewi Suryanindah Supramono, and Nabil Fadel. "Electronic Waste Generation Prediction in Bandung City, Indonesia." Environmental and Climate Technologies 25, no. 1 (January 1, 2021): 111–20. http://dx.doi.org/10.2478/rtuect-2021-0007.

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Abstract Nowadays waste electrical and electronic equipment (WEEE) generation is increasing due to the increase in the number of users and the development of electronic products. In Indonesia, there are no specific regulations about WEEE even though it is identified as hazardous and toxic waste. This study aims to predict the WEEE generation from the most used and replaced electronic products by citizens of Bandung City. The data is collected by surveying 400 families in Bandung City. Based on the survey results, there are three types of electronic products that are most used and replaced by citizens of Bandung City, which are mobile phones, laptops and televisions. The Delay Model is modified by replacing the lifespan variable with end-of-life to project the mobile phones, laptops and televisions waste generation in Bandung City. The purpose of this modification is to adjust the pattern of electronic products used in developing countries. The projection results state that Bandung City will generate 0.61 tons/day of mobile phones, 8.66 tons/day of laptops and 3.16 tons/day of televisions at the end of 2020. Based on the results of the projection, WEEE management and recycling is important which can reduce WEEE disposal and increase the economic value of WEEE.
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30

Wordsworth, Jamie, Nadia Khan, Jack Blackburn, Jason E. Camp, and Athanasios Angelis-Dimakis. "Technoeconomic Assessment of Organic Halide Based Gold Recovery from Waste Electronic and Electrical Equipment." Resources 10, no. 2 (February 20, 2021): 17. http://dx.doi.org/10.3390/resources10020017.

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Waste Electronic and Electrical Equipment (WEEE) is one of the fastest growing waste streams worldwide, with significant economic value due to the precious metals contained within. Currently, only a small share of the total globally produced quantity produced is treated effectively and a large amount of valuable non-renewable resources are being wasted. Moreover, the methods currently applied in industry on a large scale are not always environmentally friendly. Thus, an economically viable and environmentally friendly method that would achieve high recovery of certain elements is sought. The objective of this paper is to assess four different organic halides as leaching agents for gold recovery from WEEE. Two of them have been previously tested (namely N-bromosuccinimide, NBS, and N-chlorosuccinimide, NCS) and have shown promising results, whereas the other two are novel and were selected due to their lower toxicity levels (trichloroisocyanuric acid, TCICA, and tribromoisocyanuric acid, TBICA). Both commercially supplied pure gold powder and WEEE dust from a recycling company were used as the gold source. Results show that from a technical standpoint, the NBS is a superior solution with both substrates, reaching 61% and 99% extraction efficiency from WEEE dust and pure gold, respectively. The other three methods recorded lower recovery efficiency (with the highest value reaching 36% for NCS, 53% for TCICA and 29% for TBICA). However, taking into account the price of gold and the expenses of the extraction process, only three of the lixiviants tested (NBS, NCS and TCICA) could be potentially profitable and viable on a larger scale.
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31

MATSUTO, Toshihiko. "Past, Present and Future of WEEE (Waste Electrical and Equipment) Recycling." Journal of The Institute of Electrical Engineers of Japan 128, no. 11 (2008): 732–35. http://dx.doi.org/10.1541/ieejjournal.128.732.

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32

Aidonis, Dimitrios, Charisios Achillas, Dimitrios Folinas, Christos Keramydas, and Naoum Tsolakis. "Decision Support Model for Evaluating Alternative Waste Electrical and Electronic Equipment Management Schemes—A Case Study." Sustainability 11, no. 12 (June 18, 2019): 3364. http://dx.doi.org/10.3390/su11123364.

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Waste of electrical and electronic equipment (WEEE) is a constantly increasing component of the total volume of municipal solid waste. E-waste streams are expected to continue escalating in the near future. The underlining paradox lies in the fact that end-of-life electrical and electronic equipment constitute a critical waste stream owing to the contained hazardous and toxic elements, but they also present an important source of valuable raw materials. Therefore, identification of alternative scenarios for integrated WEEE management is imperative. To that end, this research develops a methodological approach that focuses on determining the optimal WEEE management scheme, among available alternatives, applicable to the specific case of Greece. In particular, a binary linear programming model is formulated that maximizes the performance of 9 alternative WEEE management scenarios. The mathematical model considers 12 performance assessment criteria identified across financial, technical, social, and environmental dimensions. Priority levels are assigned to each criterion based on the input of 19 involved experts. A range of “what-if” analyses indicate that mechanical recycling of WEEE, in tandem with exporting of residues, is the most efficient e-waste management strategy in the case of Greece. The research findings indicate that the joint cooperation of all stakeholders, together with political will and effectiveness, is required for the integrated WEEE management at a national level.
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Mota-Panizio, Roberta, Luis F. Carmo-Calado, Octávio Alves, Catarina Nobre, J. L. Silveira, Paulo Sérgio Duque de Brito, and Margarida Gonçalves. "Effect of the Incorporation of Biomass in the Carbonization of Waste Electrical and Electronic Equipment." Proceedings 52, no. 1 (April 6, 2021): 4. http://dx.doi.org/10.3390/proceedings2020052004.

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The behavior of chars from the carbonization process were studied when the lignocellulosic biomass was incorporated into the waste of electrical and electronic equipment for chlorine removal. Tests were performed at 300°C with a heating rate of 15°C/min and residence time of 60 min. Compositions studied had 100, 75, 50, 25 and 0% of waste electrical and electronic equipment (WEEE) in the mixtures. The composition of 50% WEEE with 50% lignocellulosic biomass presented the best char properties, having an increment of the calorific value in 5.5% relative to the initial value, and chlorine removal of 23.4% when compared to the forestry biomass.
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34

Kapustka, Katarzyna, Gerhard Ziegmann, and Dorota Klimecka-Tatar. "Problems in waste management in the aspect of the secondary use of plastics from WEEE." MATEC Web of Conferences 183 (2018): 01011. http://dx.doi.org/10.1051/matecconf/201818301011.

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Waste of electrical and electronic equipment is one the fastest growing waste streams in the EU, with some 9 million tonnes generated in 2005 and expected to grow to more than 12 million tonnes by 2020. Electrical and electronic products contain substances, which are valuable as well as often also critical. The main aim of the paper is presentation the methodological approach to identification of bromine or chlorine presence in components (in WEEE). This followed by assessment of strengths and weaknesses of the most popular methods. The main analysis for identification of bromine and chlorine in plastics have been presented.
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35

Yang, Xiaoning, Lushi Sun, Jun Xiang, Song Hu, and Sheng Su. "Pyrolysis and dehalogenation of plastics from waste electrical and electronic equipment (WEEE): A review." Waste Management 33, no. 2 (February 2013): 462–73. http://dx.doi.org/10.1016/j.wasman.2012.07.025.

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36

Wang, Ruixue, and Zhenming Xu. "Recycling of non-metallic fractions from waste electrical and electronic equipment (WEEE): A review." Waste Management 34, no. 8 (August 2014): 1455–69. http://dx.doi.org/10.1016/j.wasman.2014.03.004.

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37

Tarantili, P. A., A. N. Mitsakaki, and M. A. Petoussi. "Processing and properties of engineering plastics recycled from waste electrical and electronic equipment (WEEE)." Polymer Degradation and Stability 95, no. 3 (March 2010): 405–10. http://dx.doi.org/10.1016/j.polymdegradstab.2009.11.029.

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38

Alavi, Nadali, Mohammad Shirmardi, Aliakbar Babaei, Afshin Takdastan, and Nastaran Bagheri. "Waste electrical and electronic equipment (WEEE) estimation: A case study of Ahvaz City, Iran." Journal of the Air & Waste Management Association 65, no. 3 (October 20, 2014): 298–305. http://dx.doi.org/10.1080/10962247.2014.976297.

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39

Jang, Yong-Chul. "Waste electrical and electronic equipment (WEEE) management in Korea: generation, collection, and recycling systems." Journal of Material Cycles and Waste Management 12, no. 4 (November 2010): 283–94. http://dx.doi.org/10.1007/s10163-010-0298-5.

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40

Li, Jingying, Tong Xu, Jinyuan Liu, Jiangxian Wen, and Shuli Gong. "Bioleaching metals from waste electrical and electronic equipment (WEEE) by Aspergillus niger: a review." Environmental Science and Pollution Research 28, no. 33 (July 2, 2021): 44622–37. http://dx.doi.org/10.1007/s11356-021-15074-z.

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41

Grigorescu, Grigore, Iancu, Ghioca, and Ion. "Waste Electrical and Electronic Equipment: A Review on the Identification Methods for Polymeric Materials." Recycling 4, no. 3 (August 13, 2019): 32. http://dx.doi.org/10.3390/recycling4030032.

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Considering that the large quantity of waste electrical and electronic equipment plastics generated annually causes increasing environmental concerns for their recycling and also for preserving of raw material resources, decreasing of energy consumption, or saving the virgin materials used, the present challenge is considered to be the recovery of individual polymers from waste electrical and electronic equipment. This study aims to provide an update of the main identification methods of waste electrical and electronic equipment such as spectroscopic fingerprinting, thermal study, and sample techniques (like identification code and burning test), and the characteristic values in the case of the different analyses of the polymers commonly used in electrical and electronic equipment. Additionally, the quality of the identification is very important, as, depending on this, new materials with suitable properties can be obtained to be used in different industrial applications. The latest research in the field demonstrated that a complete characterization of individual WEEE (Waste Electric and Electronic Equipment) components is important to obtain information on the chemical and physical properties compared to the original polymers and their compounds. The future directions are heading towards reducing the costs by recycling single polymer plastic waste fractions that can replace virgin plastic at a ratio of almost 1:1.
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42

Ylä-Mella, Jenni, Kari Poikela, Ulla Lehtinen, Pia Tanskanen, Elisabeth Román, Riitta L. Keiski, and Eva Pongrácz. "Overview of the WEEE Directive and Its Implementation in the Nordic Countries: National Realisations and Best Practices." Journal of Waste Management 2014 (October 1, 2014): 1–18. http://dx.doi.org/10.1155/2014/457372.

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Electronic devices and mobile applications have become a part of everyday life. Fast technological progress and rapid product obsolescence have led to the rapid growth of waste electrical and electronic equipment (WEEE). Due to hazardous substances and also substantial amounts of valuable materials contained in electrical and electronic equipment, the European Union has implemented Directives related to WEEE, in order to reduce negative environmental and health impacts and to improve material recovery of valuable substances from WEEE. This paper provides an overview of the WEEE Directive and its implementation to national legislations in Finland, Sweden, and Norway and, further, describes how the nationwide WEEE recovery infrastructures in the Nordic countries have been built. The Nordic WEEE management systems are evaluated from the point of resource efficiency and best practices. Evidently, the WEEE management systems as established in the Nordic countries have advantages because the WEEE collection rates in 2012 were 12 kg/inhab./year, in Finland, 16 kg/inhab./year, in Sweden, and 27 kg/ inhab./year, in Norway, despite their sparsely populated nature. The Swedish and Norwegian experiences, especially, with long history of WEEE recovery indicate that increasing consumer awareness leads to more environmentally sound behaviour and improves recovery efficiency.
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43

Assadian, Mahtab, Mohd Hasbullah Idris, Seyed Morteza Ghaffari Shahri, and Babak Gholampour. "Gold Recovery from WEEE by Chlorine System." Applied Mechanics and Materials 330 (June 2013): 123–25. http://dx.doi.org/10.4028/www.scientific.net/amm.330.123.

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This work compared the effect of nitric acid and chloride acid systems on dissolving precious metals of Electrical and Electronic Equipments (EEE). As a result of the revolution of informatics technology, the production of EEE is rapidly increasing in the world. Due to economic growth, technological innovation and market expansion of EEE there is a significant increase in waste of EEEs (WEEE) that presents a new environmental challenge.The results show that the best recovery of gold can be obtained via aqua regia (3HCl=HNO3), with concentration of 1/10 gr/L. The reaction temperature has little effect on the extent of extraction.
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44

Lv, Jun, and Shichang Du. "Kriging Method-Based Return Prediction of Waste Electrical and Electronic Equipment in Reverse Logistics." Applied Sciences 11, no. 8 (April 15, 2021): 3536. http://dx.doi.org/10.3390/app11083536.

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In reverse logistics, the accurate prediction of waste electrical and electronic equipment (WEEE) return amount is of great significance to guide electronic enterprises to formulate a reasonable recycling plan, remanufacturing production plan and inventory plan. However, due to the uncertainty of WEEE return, it is a challenge to accurately predict the WEEE return amount of recycling sites. Differently from the existing research methods aiming at the spatial correlation of the recycling amount of recycling sites, a spatial mathematical model based on Kriging method is proposed by this paper to predict the return amount of WEEE in reverse logistics. Based on the second-order randomness of the return amount, the spatial structure of the return amount of the recycling network is analyzed. According to the principle of unbiased prediction and minimum variance, the Kriging space mathematical model of WEEE return amount is derived, and the calculation process of three variograms is given. The results of Monte Carlo simulation and the case study on J company in Shanghai show that it is effective to utilize the Kriging method-based spatial mathematical model to predict the WEEE return of reverse logistics and analyze the spatial correlation structure of each recycling site. The proposed model can accurately predict the WEEE return amounts of unknown sites as well as those of the whole area through the known site data, which provides a novel analysis method and theoretical basis for the prediction of reverse logistics return amount.
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Du, Huan Zheng, Ming Wei Shan, Hui Tian, and Bin Li. "WEEE Resource Utilization Evaluation Model Exploring in China." Applied Mechanics and Materials 768 (June 2015): 766–73. http://dx.doi.org/10.4028/www.scientific.net/amm.768.766.

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There is an increasing concern about the threat of Waste Electrical and Electronic Equipments (WEEE) generating in China. The Chinese government had made a series of regulations and policies to address this problem. However, these practices are more focusing on the environmental protection rather than the resource utilization. Since WEEE is also a valuable kind of renewable resource, this essay will try to understand the current situation of WEEE recycling and resource utilization technologies and equipments. In the year of 2014, China Household Electric Appliance Research Institute conducted a questioner research targeting the 91 subsidy funded companies, which received 50 responses. By the comparison of previous studies of this issue and the analysis of the data collected, resource utilization situation of the industry can be addressed. This essay will also explore an evaluation model to assess the resource utilization standard of WEEE recycling. Based on the analysis, nine outcome criteria and evaluation strategies are formed to judge the resource utilization standards of WEEE recycling companies. This evaluation model will target all the life cycle of WEEE, and include criteria such as recycling technology and equipment, management standard, and resource utilization level.
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46

Menad, N., S. Guignot, and J. A. van Houwelingen. "New characterisation method of electrical and electronic equipment wastes (WEEE)." Waste Management 33, no. 3 (March 2013): 706–13. http://dx.doi.org/10.1016/j.wasman.2012.04.007.

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47

Hermoso-Orzáez, Manuel Jesús, Roberta Mota-Panizio, Luis Carmo-Calado, and Paulo Brito. "Thermochemical and Economic Analysis for Energy Recovery by the Gasification of WEEE Plastic Waste from the Disassembly of Large-Scale Outdoor Obsolete Luminaires by LEDs in the Alto Alentejo Region (Portugal)." Applied Sciences 10, no. 13 (July 2, 2020): 4601. http://dx.doi.org/10.3390/app10134601.

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The recovery of urban waste is a social demand and a measure of the energy-environmental sustainability of cities and regions. In particular, waste of electrical origin, waste of electrical and electronic materials (WEEE) can be recovered with great success. The plastic fraction of these wastes allows their gasification mixed with biomass, and the results allow for producing syngas with a higher energy potential. This work allows for obtaining energy from the recovery of obsolete materials through thermochemical conversion processes of the plastic waste from the disassembly of the luminaires by mixing the said plastic waste in different proportions with the biomass of crop residues (olive). The gasification tests of these mixtures were carried out in a downstream fixed-bed drown daft reactor, at temperatures of approximately 800 °C. The results demonstrate the applied technical and economic feasibility of the technology by thermal gasification, for the production of LHV (Low Heating Value) syngas with highest power energy (more than 5 MJ/m3) produced in mixtures of up to 20% of plastic waste. This study was complemented with the economic-financial analysis. This research can be used as a case study for the energy recovery through gasification processes of plastic waste from luminaires (WEEE), mixed with agricultural biomass that is planned to be carried out on a large scale in the Alentejo (Portugal), as a solution applied in circular economy strategies.
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48

Wang, Jun Jun, and Yong Ming Wu. "Simulating Production Lines of Recycling WEEE Products in eM-Plant." Advanced Materials Research 97-101 (March 2010): 2287–90. http://dx.doi.org/10.4028/www.scientific.net/amr.97-101.2287.

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The materials and combination of Waste Electrical and Electronic Equipments (WEEE) are complex and special, so the recycling technological process of WEEE is complicated and its recycling production line is difficult to be constructed. To improve the rate of parts reuse, the purity and quality of recycling materials with lower cost, it is necessary to manually disassemble WEEE products as much as possible. The recycling production line is simulated through the eM-Plant software to find out its bottleneck procedures. The bottleneck procedures are eliminated through the method of parallel process. The production efficiency, cost, logistics, staff and flexibility of the production line are analyzed through simulation.
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49

Gu, Yifan, Yufeng Wu, Ming Xu, Xianzhong Mu, and Tieyong Zuo. "Waste electrical and electronic equipment (WEEE) recycling for a sustainable resource supply in the electronics industry in China." Journal of Cleaner Production 127 (July 2016): 331–38. http://dx.doi.org/10.1016/j.jclepro.2016.04.041.

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50

Tadic, Branko, Ratko Mitrovic, and Danijela Tadic. "The evidence of personal computer waste quantity in the territory of Serbia -statistical estimation." Ekonomski anali 51, no. 169 (2006): 127–42. http://dx.doi.org/10.2298/eka0669127t.

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In recent years, the state-of-the-art research has been dealing with putting into traffic, withdrawing and freeing the environment from electrical and electronic equipment waste-WEEE. In our country there has been no serious research so far concerning this problem, although current and future members of the European Union (EU) are obligated to conduct WEEE directive based on individual responsibility of each "waste manufacturer". The Ministry of Science and Environmental Protection of Serbia has accepted the financing of scientific research project called "The development of electrical and electronic equipment recycling system". In this paper, statistical estimation method of quantity and diffusion of computer waste (which according to the EU classification, belongs to the third category WEEE-devices for computer and communication technique) in the territory of Serbia is described. The implications of the problem on our country are also presented.
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