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Published by : http://www.ijert.org International Journal of Engineering Research & Technology (IJERT) ISSN: 2278-0181 Vol. 9 Issue 11, November-2020 E-Waste Management with respect to Indian Scenario * ** Narendra Sukhdevrao Naik *, Dr. Arif Khan** Environmental Engineering Department; Nuva College of Engineering & Technology Nagpur ,India Environmental Engineering Department ;Nuva College of Engineering & Technology Nagpur ,India Abstract- The electronic industry is the world’s largest and fastest growing manufacturing industry in the world. The increasing “market penetration” in developing countries, “replacement market” in developed countries and “high obsolescence rate” of electrical and electronic goods make electrical and electronic waste (e-waste) one of the fastest growing waste streams. E-waste is valuable source for secondary raw material but harmful if treated and discarded improperly as it contains many toxic components such as lead, cadmium, mercury, polychlorinated biphenlys etc. Electronic waste or e-waste refers to unwanted, obsolete or unusable electronic and electrical products. Ever increasing usage of electronics and electrical equipments has resulted in piling up of e-waste. The current practices of e-waste management in India encounters many challenges like the difficulty in inventorization, ineffective regulations, pathetic and unsafe conditions of informal recycling, poor awareness of consumers and reluctance on part of the stakeholders to address the issues. In this paper case study of E-Waste management in India and using some efficient methods for EWaste Management Like “RRR”.& E-waste contains a good amount of valuable recyclable materials also and has potential to become lucrative business in the country. KeywordsE-Waste, Recycling, Electronic, Reuse, Hazardous,Househlod, Landfilling, Equipments, Environmentally Sound Management. The quantity of e-waste generated in developed countries equals 1% of total solid waste on an average and is expected to grow to 2% by 2010 (UNEP Manual, 2007).In United States alone, 1,30,000 computers and 3,00,000 cell phones are trashed each day (Anderson, 2010).The developed countries use most of the world’s electronic products and generate most of the E-waste (Basel Action Network, 2002). Rather than treat e-waste in an environmentally friendly manner, the developed countries are finding an easy way out of the problem by exporting these wastes to developing economies especially, South Asian countries (Basel Action Network, 2002). The import of e-waste to the developing countries is in violation of the ban imposed by Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and their Disposal, as e-waste come under the definition of hazardous waste (Basel Convention 1992).Following this, our country, a party to the convention, banned the import of hazardous waste including e-waste into the country. But a major source of ewaste in India is illegal imports (Sathish, 2006). I. INTRODUCTION E-waste is the popular name for discarded electrical and electronic equipment with all of their peripherals at the end of their life. E-waste comprises of wastes generated from used electronic devices and household appliances which are not fit for their original intended use and are destined for recovery, recycling or disposal. Such wastes encompasses wide range of electrical and electronic devices such as computers, hand held cellular phones, personal stereos, including large household appliances such as refrigerators, air conditioners etc. The electronic industry is the world’s largest and fastest growing manufacturing industry in the world. The increasing “market penetration” in developing countries, “replacement market” in developed countries and “high obsolescence rate” of electrical and electronic goods make electrical and electronic waste (e-waste) one of the fastest growing waste streams. E-waste is valuable source for secondary raw material but harmful if treated and discarded improperly as it contains many toxic components such as lead, cadmium, mercury, polychlorinated biphenlys etc. (Bandyopadhyay, 2010). IJERTV9IS110283 (Fig.1 E-Waste Scenario) The major portion of the e-waste generated domestically as well as illegally imported are recycled in crude manner leading to pollution of the environment. Lack of legislation in our country at present is aiding this hazardous form of recycling. Therefore there is urgent need to frame and implement rules for regulating this waste and to find www.ijert.org (This work is licensed under a Creative Commons Attribution 4.0 International License.) 652 Published by : http://www.ijert.org International Journal of Engineering Research & Technology (IJERT) ISSN: 2278-0181 Vol. 9 Issue 11, November-2020 environmentally sound, economically viable methods for recycling and disposing of this necessary evil. The necessity of environmentally sound management of ewaste is brought out with the help of a case study of uncontrolled dumping of e-waste. 1.1 E-WASTEE-waste is the popular name for discarded electrical and electronic equipment with all of their peripherals at the end of their life. E-waste comprises of wastes generated from used electronic devices and household appliances which are not fit for their original intended use and are destined for recovery, recycling or disposal. Such wastes encompasses wide range of electrical and electronic devices such as computers, hand held cellular phones, personal stereos, including large household appliances such as refrigerators, air conditioners etc. 1.2 MAJOR SOURCESIndividuals and Small Businesses: The useful span of a computer has come down to about two years due to improved versions being launched about every 18 months. Often, new software is incompatible or insufficient with older hardware so that customers are forced to buy new computers. By the end of financial year 2005-06, India had an installed base of 4.64 million desktops, about 431thousand notebooks and 89 thousand servers. According to the estimates made by the Manufacturers Association of Information Technology (MAIT), the Indian PC industry is growing at a 25% compounded annual growth rate. The ewaste inventory based on this obsolescence rate and installed base in India for the year 2005 has been estimated to be 146180.00 tonne. This is expected to exceed 8,00,000tonne by 2012. There is a lack of authentic and comprehensive data on e-waste availability for domestic generation of e-waste and the various State Pollution Control Boards have initiated the exercise to collect data on e- waste generation. Sixty-five cities in India generate more than 60% of the total e-waste generated in India. Ten states generate 70% of the total e-waste generated in India. Maharashtra ranks first followed by Tamil Nadu, Andhra Pradesh, Uttar Pradesh, West Bengal, Delhi, Karnataka, Gujarat, Madhya Pradesh and Punjab in the list of e-waste generating states in India.In our country, currently some units have registered with the Ministry of Environment and Forests as possessing environmentally sound management facilities for recycling of e-waste. Large corporations, Institutions and Government: Large users upgrade employee computers regularly. Original Equipment Manufacturers (OEMs):OEMs generate e-waste when units coming off the production line do not meet quality standards, and must be disposed off. Some of the computer manufacturers contract with recycling companies to handle their electronic waste, which often is exported.Besides computers, other major e waste source is the cellular phone. II. INDIAN SCENARIO (Chart 1 State Wise E-Waste Generation In India) According to ASSOCHAM, an industrial body in India the, Compound Annual Growth Rate of electronic waste is 30%. With changing consumer behavior and rapid economic growth, ASSOCHAM estimates that India will generate 5.2 million tonnes of e-waste by 2020. The electronics industry has emerged as the fastest growing segment of Indian industry both in terms of production and exports. The share of software services in electronics and IT sector has gone up from 38.7 per cent in 1998-99 to 61.8percent in 2003-04. A review of the industry statistics show that in 1990-91,hardware accounted for nearly 50% of total IT revenues while software's share was 22%. The scenario changed by 1994-95, with hardware share falling to 38%and software share rising to 41%. This shift in the IT industry began with liberalization and the opening up of Indian markets together with which there was a change in India’s import policies vis-à-vis hardware leading to substitution of domestically produced hardware by imports. IJERTV9IS110283 III. CLASSIFICATION OF E-WASTE 3.1 COMPONENTS OF E-WASTEE-waste has been categorized into three main categories, viz. large household appliances, IT and Telecom and consumer equipment. Refrigerator and washing machine represent large household appliances, personal computer monitor and laptop represent IT and Telecom, while television represents consumer equipment. Each of these e-waste items has been classified with respect to twenty six common components, which could be found in them. These components form the “building blocks” of each item and therefore they are readily “identifiable” and “removable”. These components are metal, motor/compressor, cooling, plastic, insulation, glass, (Liquid Crystal Display) LCD, rubber, wiring/ electrical, concrete, transformer, magnetron, textile, circuit board, fluorescent lamp, incandescent lamp, heating element, thermostat, BFR-containing plastic, batteries, fluorocarbons www.ijert.org (This work is licensed under a Creative Commons Attribution 4.0 International License.) 653 Published by : http://www.ijert.org International Journal of Engineering Research & Technology (IJERT) ISSN: 2278-0181 Vol. 9 Issue 11, November-2020 (CFC/HCFC/HFC/HC), external electric cables, refractory ceramic fibers, radioactive substances and electrolyte capacitors. The kinds of components, which are found in refrigerator, washing machine, personal computers (PC) and televisions. 3.2 COMPOSITION OF E-WASTEComposition of e-waste is very diverse and differs in products across different categories. It contains more than 1000 different substances, which fall under “hazardous” and “non-hazardous” categories. Broadly, it consists of ferrous and non-ferrous metals, plastics, glass, wood & plywood, printed circuit boards, concrete and ceramics, rubber and other items. Iron and steel constitutes about50% of the e-waste followed by plastics (21%), non ferrous metals (13%) and other constituents. IV. DATA AND METHODOLOGY OF THE STUDY METHODOLOGY FOR ENVIRONMENTALLY SOUND MANAGEMENT OF E-WASTE 4.1 E-WASTE COMPOSITION AND RECYCLE POTENTIALThe composition of e-waste and its recyclable potential is specific for each appliance. In order to handle this complexity, the parts/materials found in e-waste may be divided broadly into six categories as follows: Iron and steel, used for casings and frames Non-ferrous metals, especially copper used in cables, and aluminium Glass used for screens, windows Plastic used as casing, in cables and for circuit boards Electronic components Others (rubber, wood, ceramic etc.) Overview of the composition of the appliances in the three categories mentioned earlier is given in table 1. 4.2 Assessment of Hazardousness of E-wasteThe hazardous nature of e-waste is determined by identifying the e-waste category item (identification includes the waste items and year of manufacture), identifying the e-waste composition or its components, identifying possible hazardous content in the e-waste and identifying whether the e-waste component is hazardous or the entire e-waste item is hazardous. 4.3 RECYCLING, REUSE AND RECOVERY OPTIONS- (Chart 2 Generation+of+e+waste+in+India) Non-ferrous metals consist of metals like copper, aluminium and precious metals e.g. silver, gold, platinum, palladium etc. The presence of elements like lead, mercury, arsenic, cadmium, selenium and hexavalent chromium and flame retardants beyond threshold quantities in e-waste classifies them as hazardous waste. (Chart 3 Weighted-Percentage-of-Material-in-E-waste) IJERTV9IS110283 The composition of e-waste consists of diverse items like ferrous and non-ferrous metals, glass, plastic, electronic components and other items and it is also revealed that ewaste consists of hazardous elements. Therefore, the major approach to treat e-waste is to reduce the concentration of these hazardous chemicals and elements through recycle and recovery. In the process of recycling or recovery, certain e-waste fractions act as secondary raw material for recovery of valuable items. The recycle and recovery includes the following unit operations. (i) Dismantling Removal of parts containing dangerous substances (CFCs, Hg switches, PCB); removal of easily accessible parts containing valuable substances(cable containing copper, steel, iron, precious metal containing parts, e.g. contacts). (ii) Segregation of ferrous metal, non-ferrous metal and plastic This separation is normally done in a shredder process. (iii) Refurbishment and reuse Refurbishment and reuse of e-waste has potential for those used electrical and electronic equipments which can be easily refurbished to put to its original use. (iv) Recycling/recovery of valuable materials Ferrous metals in electrical are furnaces, non-ferrous metals in smelting plants, precious metals in separating works. www.ijert.org (This work is licensed under a Creative Commons Attribution 4.0 International License.) 654 Published by : http://www.ijert.org International Journal of Engineering Research & Technology (IJERT) ISSN: 2278-0181 Vol. 9 Issue 11, November-2020 (v) Treatment/disposal of dangerous materials and waste Shredder light fraction is disposed of in landfill sites or sometimes incinerated (expensive), CFCs are treated thermally, PCB is incinerated or disposed of in underground storages, Hg is often recycled or disposed of in underground landfill sites. cadmium and mercury are emitted in diffuse form or via the landfill gas combustion plant. Although the risks cannot be quantified and traced back to e-waste, landfilling does not appear to be an environmentally sound treatment method for substances, which are volatile and not biologically degradable (Cd, Hg, CFC), persistent (PCB) or with unknown behaviour in a landfill site (brominated flame retardants). As a consequence o fthe complex material mixture in e-waste, it is not possible to exclude environmental (long-term) risks even in secured landfilling. V. TREATMENT & DISPOSAL OF EWASTE The presence of hazardous elements in e-waste offers the potential of increasing the intensity of their discharge in environment due to landfilling and incineration. 5.2 IncinerationAdvantage of incineration of e-waste is the reduction of waste volume and the utilization of the energy content of combustible materials. Some plants remove iron from the slag for recycling. By incineration some environmentally hazardous organic substances are converted into less hazardous compounds. Disadvantage of incineration are the emission to air of substances escaping fluegas cleaning and the large amount of residues from gas cleaning and combustion. The potential treatment & disposal options based on the composition are given below: 1. Incineration 2. Landfilling 5.1 LandfillingThe literature review reveals that degradation processes in landfills are very complicated and run over a wide time span. At present it is not possible to quantify environmental impacts from E-waste in landfills for the following reasons: Landfills contain mixtures of various waste streams Emission of pollutants from landfills can be delayed for many years. One of the studies on landfills reports that the environmental risks from landfilling of e-waste cannot be neglected because the conditions in a landfill site are different from a native soil, particularly concerning the leaching behavior of metals. In addition it is known that There is no available research study or comparable data, which indicates the impact of e-waste emissions into the overall performance of municipal waste incineration plants. Waste incineration plants contribute significantly to the annual emissions of cadmium and mercury. In addition, heavy metals not emitted into the atmosphere are transferred to slag and exhaust gas residues and can reenter the environment on disposal. Therefore, e-waste incineration will increase these emissions, if no reduction measures like removal of heavy metals from are taken. Table 1 Average Weight and Composition of Selected Appliances (Typical) Appliances Average weight (kg) Refrigerators freezers Fe % Non Fe- Glass weight metal % weight weight % Plastic weight % Electronic components weight Others % weight and 48 .0 64.4 6 .0 1.4 13 .0 0.2 15.0 Personal computer 29.6 20.0 24 15 23.0 17.3 0.7 TV sets 36.2 5.3 5.4 62 22.9 0.9 3.5 % Table 2 Possible Hazardous Substances in Components of E-waste Component Metal Motor/compressor Cooling Plastic Insulation Glass Cathode Ray Tube Liquid Crystal Display Rubber Wiring / electrical Concrete Transformer IJERTV9IS110283 Possible hazardous content Ozone Depleting Substances (ODS) Phthalate plasticizer, brominated flame retardants (BFR) Insulation ODS in foam, asbestos, refractory ceramic fiber Lead, Antimony, Mercury, Phosphor Mercury Phthalate plasticizer, BFR Phthalate plasticizer, BFR, Lead www.ijert.org (This work is licensed under a Creative Commons Attribution 4.0 International License.) 655 Published by : http://www.ijert.org International Journal of Engineering Research & Technology (IJERT) ISSN: 2278-0181 Vol. 9 Issue 11, November-2020 Circuit Board Fluorescent lamp Incandescent lamp Heating element Thermostat BFR-containing plastic Batteries CFC,HCFC,HFC,HC External electric cables Electrolyte capacitors Lead, Beryllium, Antimony, BFR Mercury, Phosphorous, Flame retardants Mercury BFRs Lead, Lithium, Cadmium, Mercury ODS BFRs, plasticizers Glycol, other unknown substances VI. CONCLUSION The problem of E-waste is growing in alarming proportions in India as also in the world. Although many developed countries have established welldefined E-waste management systems, the systems in India have barriers from socioeconomic, infrastructural, and legal reasons. The E-waste recycling and recovery options practiced in India are very outdated and hazardous, causing severe environmental and occupational hazards Electronic and electrical equipments cannot be avoided in today’s world. So also is the case of waste electronic and electrical equipments. As long as this is a necessary evil, it has to be best managed to minimize its adverse impacts on environment. Through innovative changes in product design under EPR, use of environmentally friendly substitutes for hazardous substances, these impacts can be mitigated. A legal framework has to be there for enforcing EPR, RoHS for attaining this goal. Adoption of environmentally sound technologies for recycling and reuse of e-waste along with EPR and RoHS offers workable solution for environmentally sound management of e-waste. REFERENCES [1] [2] [3] [4] [5] [6] [7] [8] [9] [10] [11] [12] [13] [14] [15] [16] [17] [18] [19] [20] [21] [22] [23] [24] [25] [26] [27] [28] Bandhopadhyay, A. (2010) “Electronic Waste Management: Indian Practices and Guidelines” International Journal of Energy and Environment 1(5) pp. 193-807 Basel Convention on the Control of Transboundary Movement of Hazardous Wastes and Their Disposal – Document accessed in 10/2010 E-Waste Volume II, E-Waste Management Manual – United Nations Environment Program – accessed in 10/2010 Kurian Joseph (2007), “Electronic Waste Management in India-Issues and Strategies” Proc. On Eleventh International Waste Management and Landfill Symposium Mark Anderson (2010) What an E-waste” IEEE-spectrum, September, 2010 Nnorom I.C., Osibanjo O (2008) “Overview of Electronic Waste (e-waste) Management Practices and Legislation in the Developed Countries” Journal of Resource Conservation and Recycling 52(2008) 843-858 Sathish Sinha (2006) E-waste Time to Act Now –Toxic Alert, accessed in 10/2010 8)The Basel Action Network “Exporting Harm – The High Tech Trashing of Asia” accessed in 10/2010 Waste Water Engineering (2003), Metcalf and Eddy fourth edition www.moef.nic.in- website of Ministry of Environment and Forests, Government of India. BAN (2002). The Basel Action Network (BAN), the Silicon Valley Toxics Coalition (SVTC), Toxics Link India, SCOPE (Pakistan), Greenpeace China. Exporting harm: The high-tech trashing of Asia. Seattle, WA, and San Jose, CA; February 25th 2002. Chen, P. (2004). WEEE recycling and legislation development in China. In Conference paper, Electronics Goes Green 2004, 6–8 September, Berlin. Cui, J. (2005). Compiled from data presented in “Mechanical Recycling of Consumer Electronic Scrap. Licentiate Thesis 2005:36, Luleå University of Technology, Luleå, Sweden.” Cui.j SEPA (1995). P.R.C. State Environmental Protection Administration, Law on the prevention of environmental pollution from solid waste. PRC Presidential Order, No. 58, October 30, 1995. NDRC (2004). P.R.C. National Development and Reform Commission (NDRC). Ordinance on the management of waste household electrical and electronic products recycling and disposal (Draft). NDRC Express, September 19, 2004. UNEP (2007). United Nations Environment Programme: E-waste Assessment Manual. Khetriwal, D. S., Kraeuchi, P., & Schwaninger, M. (2005). A comparison of electronic waste recycling in Switzerland and in India. Journal of Environmental Impact Assessment Review, 25, 492–504 Jayant, A., Gupta, P., & Garg, K. S. (2012). Perspectives in Reverse Supply Chain Management( R-SCM): A State of the Art Literature Review. Jordan Journal of Mechanical and Industrial Engineering , 6 (1), 87-102. Jennifer, C. (2005). Distancing the waste: Overconsumption in a global economy. Retrieved september 30, 2014, from http://www.learningace.com/doc/2458434/9b350d1c37cc689f75b53752f46 5c68e/rprnts 2005-10-10clapp Joseph, K. (2007). Electronic Waste Management In India :Issues and Strategies. Eleventh International Waste Management and Landfill Symposium. Italy: CISA, Environmental Sanitary Engineering Centre, Italy. Karishma, & Vrat, P. (2015). SWOT analysis of E-waste Manageent in India. Industrial Enngineering Journal , 27-39. [15] Kumar, A., & Kumar, P. (2012). E-Waste Management in India: Issues and Options. International Journal of Languages, Education and Social Sciences, , 2 (1), 1-10. Lundgren, K. (2012). The global impact of e-waste:addressing the challenge. Geneva: International Labour Organization . MAIT-GTZ. (2007). E-waste Inventorization in India, MAIT-GTZ study. [18] Martin Streicher-Porte, R. W. (2005). Key drivers of the e-waste recycling system: Assessing and modelling e-waste processing in the informal sector in Delhi. Environmental Impact Assessment , 472-491. Meyer, H. (1999). Many happy returns. Journal of Business Strategy , 7 (80), 27-31. MoEF. (2011). Final Guidelines on Implementation of E-waste rules 2011. Retrieved october 13, 2014, from cpcb.nic.in: http://cpcb.nic.in/e_Waste.php. [21] Molinari, L. (2012). Reducing E-Waste of Consumer Electronics Through Reverse Logistics. Retrieved October 5, 2014, from www.reverselogisticstrends.com: www.reverselogisticstrends.com/productview.php?id=1216 Monika, & Kishore, J. (2010). E-waste management: Aa a challenge to Public Health in India. Indian Journal of community medicine , 382-385. Morris, B. (2010). Going Green: Best Practices for Managing and Preventing e-Waste. IJERTV9IS110283 www.ijert.org (This work is licensed under a Creative Commons Attribution 4.0 International License.) 656