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Numfor, S.; Zhang, Z.; Omosa, G. ELVs Recycling in Developing Countries. Encyclopedia. Available online: https://encyclopedia.pub/entry/10992 (accessed on 23 April 2024).
Numfor S, Zhang Z, Omosa G. ELVs Recycling in Developing Countries. Encyclopedia. Available at: https://encyclopedia.pub/entry/10992. Accessed April 23, 2024.
Numfor, Solange, Zhengyang Zhang, Geoffrey Omosa. "ELVs Recycling in Developing Countries" Encyclopedia, https://encyclopedia.pub/entry/10992 (accessed April 23, 2024).
Numfor, S., Zhang, Z., & Omosa, G. (2021, June 18). ELVs Recycling in Developing Countries. In Encyclopedia. https://encyclopedia.pub/entry/10992
Numfor, Solange, et al. "ELVs Recycling in Developing Countries." Encyclopedia. Web. 18 June, 2021.
ELVs Recycling in Developing Countries
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End-of-life vehicle is a vehicle that has reached the end of its useful life and requires proper treatment.

end-of-life vehicle (ELV) recycling developing countries emerging economies challenges opportunities

1. Introduction

The reuse and recycling of end-of-life vehicles (ELVs) has made these vehicles a vital source of secondary raw materials for use in industry [1]. This helps in closing the sustainable resources loop and decreases the demand for primary raw materials. In the wake of the regulations for the recycling of ELVs through the 2000 European Union Directive (EU Directive), many countries have implemented similar policies, with efficiencies varying from country to country [2][3]. The EU Directive on ELVs considers the environmentally friendly dismantling of ELVs, the methods for recycling, and also has clear targets for the reuse, recovery, and recycling of ELVs and their components [3]. According to the EU Directive 2000/53/EC (the ELV Directive), vehicle manufacturers are required to minimize the use of such hazardous materials as mercury, lead, hexavalent chromium, and cadmium in the production of vehicles [3][4]. In addition, the EU member states are required to set up ELV collection systems and transfer these ELVs to established authorized treatment facilities. This directive is designed to reduce contamination in the environment and to curb emissions, as well as to facilitate recycling and reduce the need for the proper disposal of these hazardous substances [4].

Some EU member states have made significant advances implementing ELV recycling measures. According to a report by the United States Environmental Protection Agency, the producer responsibility scheme in Sweden, a pioneer in ELV recycling in Europe, requires vehicle manufacturers to collect ELVs at no cost to the vehicle owner, and also to establish a management system [5]. Also, the Dutch automobile industry established the Auto Recycling Netherland (ARN) company for the collection of scrap cars, management of ELV dismantling and recycling, by partnering with vehicle dismantling companies [6]. This company is financed through the collection of waste disposal fees as part of the vehicle registration process. It was also reported that, approved ELV centers in each prefecture in France, are responsible for ELV recycling and issuing a certificate of destruction to the ELV holders [7]. In addition, each vehicle manufacturer must establish a network of authorized ELV collection and distribution centers across the country.

2. End-of-Life Vehicle Recycling in Developing Countries and Emerging Economies

According to the United Nations Conference on Trade and Development, and the United Nations World Economic Situation Prospects, country classification, Cameroon, Kenya, Nigeria, Egypt, India, Malaysia, Mexico, South Africa, are listed as developing countries [8][9]. Due to the low incomes and poor public transport infrastructure, most developing countries import second-hand vehicles [10]. Since many of these second-hand vehicles are barely roadworthy when they arrive in the country, and they are then driven on poorly maintained roads, many of them reach the end of their useful lives after a short period of use. In Kenya, ELVs are stockpiled at police station yards, despite the potential for these unclaimed stockpiled ELVs to be utilized as sources of secondary materials through recycling [11]. In Egypt, financial incentives are being offered to the owners of automobiles in a national program to promote ELV scrapping and recycling [12]. Through this program, many older taxis have been replaced with new vehicles. However, the Central Bank restricted access to foreign exchange to prevent the further devaluation of the Egyptian pound, resulting in a downturn in businesses and other economic activities in the country [13]. In Central African countries like Cameroon, little attention is given to recycling and waste management [14]. In such countries, vehicles are abandoned or disposed of illegally, and the dismantling of these vehicles is undertaken by the informal sector.

The management of ELVs in developing countries has been investigated in some studies. In their investigation into the management of automobile waste in developing countries, Nwachukwu et al. reported that a properly developed concept of mechanical village is an opportunity for developing countries to implement environmentally friendly automobile waste management [15]. However, given the underdevelopment of mechanical villages in developing countries, the authors suggested that the United Nations and automobile exporters should consider assisting developing countries to establish environmentally friendly mechanical villages. In another study on the sustainability of ELV recycling in India, Nitish et al. revealed that while weak legislation, ambiguous vehicle deregistration were impediments to progress, the setting up of automotive industry standards to regulate the types of material used in vehicles and minimum rates for reuse, recovery, and recycling of ELVs was a promising development [16]. The United Nations Industrial Development Organization (UNIDO) also stressed that it was vital to work towards establishing a circular economy by promoting recycling and recycling industries in developing countries due to the many serious waste management system challenges and pressures faced by those countries [17]. UNIDO further reported that the low cost of labor cost and the existence of strong (though informal) recovery and remanufacturing sectors provides a competitive advantage in these countries for further development, providing efforts are properly controlled.

3. ELV Recycling Activities

The reprocessing of the materials in ELVs requires the vehicles to be collected, to be depolluted, and dismantled, the materials to be sorted and shredded before being thermochemically processed, and the disposal of some of the material [18][19]. A flowchart for the environmentally sound process of recycling ELVs is provided in Figure 1 below, where processes are in plain shapes and outcomes in grey shapes.

Sustainability 13 04918 g001 550

Figure 1. Flow chart for ELV processing.

4. Strengths

The SWOT analysis of strengths per country is shown in Figure 2. In this case, a higher rating indicates that the country is in a stronger position with regard to the recycling of ELVs. As vehicles are manufactured in India and Mexico, they have been rated 2 for this category. Also, Malaysia and South Africa have been rated 1.5 for this category, because of the assembling of vehicles and manufacturing of vehicle components in these countries. Along with South Africa, these countries have higher ratings, at 1.3, for their vehicle registration systems, 1 for ELV legislation and ELV recycling, based on the infrastructure in place in these countries, and 1.5 for waste management. Egypt was also assigned a rating of 1.5 in response to its cash reward initiative for buying low emission cars. As can be seen in Figure 2, Nigeria, Kenya, and Cameroon were assigned low ratings. The strengths of developing countries classified as emerging economies, excluding Nigeria, were rated more highly than countries not considered to have emerging economies.

Sustainability 13 04918 g003 550

Figure 2. Strengths per country.

5. Weaknesses

The results of the SWOT analysis with regard to weaknesses are shown in Figure 3. The results of the SWOT analysis with regard to weaknesses are shown in Figure 3. Here, a lower rating equates to a higher weakness except for environmental impact and pollution, and unavailability of information on ELVs, where a higher rating equates to a higher weakness. The technological capacity in Mexico, Malaysia, and India was the highest, at 1.5 considering their level of vehicle manufacturing and development. South Africa was rated 1, and Nigeria, Egypt, Kenya, and Cameroon were rated poorly. Among the developing countries, those acknowledged to be emerging economies had greater technological capacities for application to the recycling of ELVs. The recycling infrastructure in India, Malaysia, Mexico, and South Africa was 1, the ELV regulatory framework was rated at 0.8. This was followed by Egypt, Nigeria, Kenya, and Cameroon. In the case of the waste regulatory framework, South Africa, Mexico, and Malaysia were rated at 1.5, and India, Egypt, Nigeria, Kenya, and Cameroon were rated lower. The countries with emerging economies were rated at 0.9 for ELV collection, and Egypt was rating at 0.8, considering the cash reward incentive. The rating for Nigeria was 0.3, and Kenya and Cameroon were rated 0.2. The environmental impact and pollution due to ELVs were the worst in Cameroon, Kenya, and Nigeria due to the lack of ELV recycling. The environmental impact and pollution from ELVs were also shown to be a problem in Egypt, and the other emerging economies. Limited information on ELVs was a problem in all of the countries. South Africa and Egypt were rated well for their small efforts to extend producer responsibility and the cash incentives, respectively.

Sustainability 13 04918 g004 550

Figure 3. Weaknesses per country.

6. Opportunities

Here, the higher the rating, the greater the opportunity. Given its large population size, India was considered to have the highest opportunity rating, at 2 for its large market size and informal sector, and 1.5 for ELV parts recyclers. Egypt, Kenya, and Cameroon had low ratings of 0.8, and 0.7 for ELV parts recyclers, respectively. Since they have some companies engaging in the recycling of ELV parts, Nigeria, South Africa, Mexico, and Malaysia were considered to have greater opportunities. The potential market size was gauged by the population of the countries: India is seconded by Nigeria, and then Mexico, Egypt, South Africa, Kenya, Malaysia, and Cameroon. The scale of the informal sector was considered a valuable opportunity for all the countries, especially for India. Labor from the large informal sector could be used in a healthy and occupational safety approach, for deep dismantling of ELVs as a means to recover some high-quality materials such as glass, copper, batteries, aluminum, catalytic converters, and plastics [16]. The low cost of labor was considered a valuable opportunity for ELV investment in these countries. This is particularly true in Cameroon, where the cost of labor is the lowest. All countries were deemed to have considerable opportunities with regard to their potential for ELV recycling (Figure 4).

Sustainability 13 04918 g005 550

Figure 4. Opportunities per country.

7. Threats

A higher rating equates to a higher threat. The lack of attention to ELV recycling by the governing authorities was the most problematic in Cameroon, Kenya, and Nigeria, followed by Egypt. Political and social instability was also high for Cameroon and Nigeria, and the difficulty of doing business was very high in Cameroon, Nigeria, and Egypt. Kenya followed these countries. Meanwhile, Mexico, Malaysia, and India were rated fairly for their lack of attention to ELV recycling, political and social instability, and difficulty of doing business. Malaysia was shown to have the most favorable business regulation with its low rate of difficulty of doing business. In the category of “Threats”, all countries were shown to be susceptible to specific threats identified ( Figure 5).

Sustainability 13 04918 g006 550

Figure 5. Threats per country.

References

  1. Kosacka-Olejnik, M. How manage waste from End-of-Life Vehicles?—Method proposal. IFAC 2019, 52, 1733–1737.
  2. Despeisse, M.; Kishita, Y.; Nakano, M.; Barwood, M. Towards a circular economy for end-of-life vehicles: A comparative study UK–Japan. Procedia CIRP 2015, 29, 668–673.
  3. European Commission Environment. End of Life Vehicles. Available online: (accessed on 7 April 2021).
  4. European Parliament and Council. Directive 2000/53/EC of the European Parliament and of the Council of 18 September 2000 on end-of life vehicles. Off. J. Eur. Communities 2000, 5, 34–43.
  5. Rovinaru, F.I.; Rovinaru, M.D.; Rus, A.V. The Economic and Ecological Impacts of Dismantling End-of-Life Vehicles in Romania. Sustainability 2019, 11, 6446.
  6. United States Environmental Protection Agency. Recycling and Resuse: End-of-Life Vehicles and Producer Responsibility. Available online: (accessed on 7 April 2021).
  7. Agence de l’Environnement et de la Maitrise de l’Energie. Annual Report the End-of-Life Vehicle Observatory Report. 2017. Available online: (accessed on 7 April 2021).
  8. United Nations Conference on Trade and Development. Country Classification. Available online: (accessed on 7 April 2021).
  9. United Nations. World Economic Situation Prospects. Country Classification. New York. 2020. Available online: (accessed on 7 April 2021).
  10. Agbo, C.O.A. Recycle materials potential of imported used vehicles in Nigeria. Niger. J. Technol. 2011, 30, 118–128.
  11. Muiruri, J.K. The magnitude of unclaimed end of life vehicles and environmental implications in police stations’ yards: A case study of Nairobi, Kenya. Am. J. Environ. Prot. 2014, 3, 51–58.
  12. The World Bank. Scrapping and Recycling Old Vehicles in Egypt. 2015. Available online: (accessed on 7 April 2021).
  13. Springborg, R. Egypt’s economic transition: Challenges and prospects. In Combining Economic and Political Development; Graduate Institute Publications: Geneva, Switzerland; Brill Nijhoff: Boston, MA, USA, 2017; pp. 184–210.
  14. Global Recycling. The Magazine for Business Opportunities and International Markets. Available online: (accessed on 7 April 2021).
  15. Nwachukwu, M.A.; Feng, H.; Achilike, K. Integrated studies for automobile wastes management in developing countries; in the concept of environmentally friendly mechanic village. Environ. Monit. Assess. 2011, 178, 581–593.
  16. Arora, N.; Bakshi, S.K.; Bhattacharjya, S. Framework for sustainable management of end-of-life vehicles management in India. J. Mater. Cycles Waste Manag. 2019, 21, 79–97.
  17. Development of Recycling Industries within the UNIDO Circular Economy Approach. UNIDO. Vienna. 2019. Available online: (accessed on 7 April 2021).
  18. Chen, K.; Huang, S.; Lian, I. The development and prospects of the end-of-life vehicle recycling system in Taiwan. Waste Manag. 2010, 30, 1661–1669.
  19. Hedayati, M.; Subic, A. A framework for extended end-of-life vehicle (ELV) recovery rate based on a sustainable treatment option. Int. J. Sustain. Des. 2011, 1, 381–401.
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