A Review on Global E-Waste Management: Urban Mining towards a Sustainable Future and Circular Economy
Abstract
:1. Introduction
2. Global E-Waste Statistics and Value
3. The World Health Organization (WHO) Report 2021: Children and Digital Dumpsites
4. Natural Resources and Depletion Rate
5. International Conventions, Regulations and Laws
6. The Basel Convention
7. Achieving UN Sustainable Development Goals (SDGs) and E-Waste
- SDG 3: Good health and well-being,
- SDG 6: Clean waste and sanitation,
- SDG 8: Decent work and economic growth,
- SDG 11: Sustainable cities and communities
- SDG 12: Responsible consumption and production and
- SDG 14: Life below water
8. E-Waste Legislations across the Globe
8.1. Asia
8.2. The Americas
8.3. Europe
8.4. Africa
8.5. Oceania
9. Extended Producer Responsibility (EPR) and Producer Responsibility Schemes across the Globe
- 1.
- Product take-back: This tool assigns responsibility for product end-of-life management to manufacturers or merchants. This is frequently accomplished by setting collecting and recycling goals for a product. Producers may choose to do an obligatory or voluntary takeback. Producers might also meet their goals by offering consumers incentives for returning unwanted products to a reputable merchant.
- 2.
- Economic and market-based instruments provide a monetary incentive for the implementation of EPR policies. They are available in four different forms:
- Deposit-refund: At the time of purchase, the buyer must pay a deposit, which is partially or totally recovered when the goods is returned to the producer/retailer at a defined location.
- Advanced disposal fees (ADF): Consumers are paid a price at the time of purchase for specific items depending on expected collection and treatment expenses. The charge is collected by either governmental or private bodies and used to fund the post-consumer treatment of the items in question. Consumers may be reimbursed for unused costs.
- Material tax: This is a tax paid on manufacturers who use virgin materials, difficult-to-recycle materials, or hazardous materials, in order to encourage them to use secondary (recycled) or less harmful resources. The tax should ideally be set at a level that covers the treatment expenses. Post-consumer items are collected, sorted and treated with the help of the tax.
- Upstream combination tax/subsidy (UCTS): This is a tax that is levied on manufacturers and then used to finance garbage treatment. It also offers businesses with incentives to change the design and materials of their products, as well as a finance plan to encourage recycling and treatment.
- 3.
- Regulations and performance standards imposed on producers can compel them to employ a minimum number of recycled materials, which can stimulate the return and recycling of end-of-life items. When combined with a fee, such rules can help to improve incentives for product redesign. The industries themselves might implement performance criteria that are either mandated or voluntary.
- 4.
- Information-based instruments are meant to raise public knowledge of EPR programs and thereby indirectly support them. Labeling items and components, communicating with customers about producer responsibility and waste separation and notifying recyclers about the materials used in products are all examples of possible measures [14,24,25,26] (Rashmi and Seeram 2020).
10. Health Hazards and Environmental Impacts
- cheap labor,
- illiteracy rate,
- lack of policy enforcement,
- lack of statistics on the amount of E-waste generated,
- lack of formal infrastructure,
- lack of awareness among stakeholders,
- inadequate individual and social responsibilities,
- dominance of informal sector.
11. Urban Mining V/S Virgin Mining
12. Entrepreneurship and Expertise
13. Discussion on the Global Challenges and Opportunities in a Structured E-Waste Management
- Legal Framework: The gaps and solutions with respect to the current policies are explained below.
- Cheaper than virgin mining,
- More sustainable and effective,
- Help preserve natural resources,
- No harm to the environment as it takes place in a controlled system,
- Health and safety of women and children are protected,
- Helps achieve a decarbonized circular economy.
- 2.
- Benchmark Technology: Although E-waste legislation is the main path for the transition towards a circular economy, state of the art infrastructure and benchmark technologies also play an important role. The resources, hazards and impacts for E-waste generated are the same across the globe, but each country has a different processing system. There is an immediate need for the international leaders to review the global best technological practices carried out to arrive at a benchmark technology for each of the processing cycles of E-waste [49,50,51]. Innovation may be the key to come up with indigenous technology for recycling, re-use, repair, refurbishment and component harvesting to extend the life spans of the products and components and to optimize and increase the outputs of E-waste processing plants. This would also help us achieve transparency and avoid illegal methods of handling E-waste.
- 3.
- Implementation of EPR: Even when the chemistry of the product remains the same and producers use the same resources, the EPR policy differs greatly between OECD and non-OECD countries, thus creating complex issues in E-waste management. Stakeholders are not aware of the roles and responsibilities because of the confusion in policies varying across the globe. To establish a legal and environment-friendly sound management of E-waste, stringent adoption of a mandated universal EPR law across the globe is critical. Implementation of a common law will make sure generators and manufacturers are aware of their responsibilities and will act accordingly without conflicts.
- 4.
- Green policies such as Green Product Identification should be enforced mandatorily, where the producers are responsible for identifying the chemistry of their product and making sure that each component manufactured can be harvested at their end-of-life. Clearly, enforcement of EPR is very essential in order to drive the stakeholders towards responsible design of products, production and processing of the recycled E-waste. Such practices can only be fruitful when the government supports and encourages the formal system of E-waste management by facilitating their needs through financial, technological or expert support.
- 5.
- Consumer Behavior: While manufacturers and generators need to act responsibly, there is a need for consumers to also play a role in disposing their E-waste responsibly. Regulating the manufacturers to give comprehensive information about each product to the consumers containing information about the composition, hazards of improper disposal, practices of re-use, repair and refurbishment, life span of the product, etc., can bring a significant change in the way consumers view their contributions to a greener environment. In addition, awareness activities need to be conducted for consumers on the effects of illegal dumping of E-waste.
- 6.
- Transformation of the Informal Sector: Unsustainable methods of handling E-waste have created a problem the size of a planet. Women and children from the illiterate sections of society are used for dismantling E-waste. Processes such as manual stripping of cables, lack of safety gear, open incineration and acid leaching have led to various diseases and caused irreparable damage to the environment. Due to a significant dominance of the informal sector handling E-waste (Figure 4), it is a grave task to educate and transform them about the hazards caused due to their illegal and unorthodox methods of processing the E-waste. Formalizing them would solve 90% of the problems caused to the environment by E-waste and would be easy to trace and maintain transparency on the amount of E-waste generated and processed.
14. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Conflicts of Interest
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Precious Metal | Quantity Available in Below-Ground Reserves (Tons) | Annual Consumption Rate (Tons) | Depletion Period (Years) | Major Regions of Source |
---|---|---|---|---|
Gold | 50,000 | 4400 | 11 | South Africa, USA, Indonesia |
Silver | 503,000 | 33,000 | 15 | Peru, Australia, Poland |
Platinum | 69,000 | 252 | 19 | South Africa, Russia, Zimbabwe |
Copper | 870,000,000 | 28,000,000 | 31 | Chile, Mexico, USA, Indonesia |
Region | Annual E-Waste Generation (Mt) | Percentage of E-Waste Generation (%) | E-Waste (kg/Person) |
---|---|---|---|
Asia | 24.9 | 46.5 | 5.6 |
The Americas | 13.1 | 24.4 | 13.3 |
Europe | 12 | 22.4 | 16.2 |
Africa | 2.9 | 5.4 | 2.5 |
Oceania | 0.7 | 1.3 | 16.1 |
E-Waste Component | Process Followed by Informal Sectors | Potential Health Hazard | Potential Environmental Impact |
---|---|---|---|
Cathode Ray Tubes (CRT) | Breaking of the copper yoke, removal of copper yoke and openly discarding it in landfills |
| Leaching of heavy metals such as lead, barium and others into groundwater, as well as the release of toxic phosphorus |
Printed Circuit Boards (PCBs) | De-soldering and separating computer chips |
| Probable emission of the exact substances in to the atmosphere |
Dismantled PCB Processing | Open incineration of PC boards | Toxicity of tin, lead, brominated dioxin, beryllium, cadmium and mercury inhalation in employees and nearby residents | Brominated dioxins, beryllium, cadmium and mercury inhalation, as well as tin and lead pollution of the nearby environment, including surface and groundwater |
Gold-Plated Substances and other Chips | Chemical stripping of contaminants along riverbanks with nitric and hydrochloric acid |
|
|
Plastics from the computer and peripherals | Lower temperature melting and Shredding | Workers living in the burning operations vicinity may have been exposed to hydrocarbons, brominated dioxin and PAH. | Brominated dioxins, heavy metals and hydrocarbons emissions in to the atmosphere |
Smelting of secondary steel, copper and precious metals | Steel or copper is recovered from waste in the furnace. | Dioxins and heavy metals may be exposed to workers | Dioxins and heavy metals are released into the environment, contaminating the air. |
Wires | Open incineration for the recovery of copper | Workers living in the burning operations vicinity may have been exposed to brominated and chlorinated dioxin and PAH | Discharge of hydrocarbons and ashes, including PAHs, into the air, water and soil |
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Murthy, V.; Ramakrishna, S. A Review on Global E-Waste Management: Urban Mining towards a Sustainable Future and Circular Economy. Sustainability 2022, 14, 647. https://doi.org/10.3390/su14020647
Murthy V, Ramakrishna S. A Review on Global E-Waste Management: Urban Mining towards a Sustainable Future and Circular Economy. Sustainability. 2022; 14(2):647. https://doi.org/10.3390/su14020647
Chicago/Turabian StyleMurthy, Venkatesha, and Seeram Ramakrishna. 2022. "A Review on Global E-Waste Management: Urban Mining towards a Sustainable Future and Circular Economy" Sustainability 14, no. 2: 647. https://doi.org/10.3390/su14020647
APA StyleMurthy, V., & Ramakrishna, S. (2022). A Review on Global E-Waste Management: Urban Mining towards a Sustainable Future and Circular Economy. Sustainability, 14(2), 647. https://doi.org/10.3390/su14020647