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1 | P a g e
OPEN ACCESS JOURNAL 2021
All About E-Waste Management in the World
Prof Alex Walter, USA
Abstract- Electronic waste or e-waste describes discarded electrical or electronic devices.
Used electronics which are destined for refurbishment, reuse, resale, salvage recycling through
material recovery, or disposal are also considered e-waste. Informal processing of e-waste in
developing countries can lead to adverse human health effects and environmental pollution.
Electronic scrap components, such as CPUs, contain potentially harmful materials such as lead,
cadmium, beryllium, or brominated flame retardants. Recycling and disposal of e-waste may
involve significant risk to health of workers and their communities.
Keywords- e-waste, waste, management.
Introduction
E-waste or electronic waste is created when an electronic product is discarded after the end of
its useful life. The rapid expansion of technology and the consumption driven society results
in the creation of a very large amount of e-waste. The European Waste Electrical and Electronic
Equipment Directive Directive classifies waste in ten categories: Large household appliances
(including cooling and freezing appliances), Small household appliances, IT equipment
(including monitors), Consumer electronics (including TVs), Lamps and Luminaires, Toys,
Tools, Medical devices, Monitoring and control instruments and Automatic dispensers. These
include used electronics which are destined for reuse, resale, salvage, recycling, or disposal as
well as re-usables (working and repairable electronics) and secondary raw materials (copper,
steel, plastic, etc.). The term "waste" is reserved for residue or material which is dumped by
the buyer rather than recycled, including residue from reuse and recycling operations, because
loads of surplus electronics are frequently commingled (good, recyclable, and non-recyclable).
Several public policy advocates apply the term "e-waste" and "e-scrap" broadly to all surplus
electronics. Cathode ray tubes (CRTs) are considered one of the hardest types to recycle.[2]
On the other hand, the Partnership on Measuring ICT for Development defines e-waste into six
categories, namely : (1) Temperature exchange equipment (e.g., air conditioners, freezers), (2)
Screens, monitors (e.g., TV, laptop), (3) Lamps(e.g., LED lamps), (4) Large equipment (e.g.,
washing machines, electric stoves), (5) Small equipment (e.g., microwave, electric shaver), and
(6) Small IT and telecommunication equipment (e.g., mobile phones, printers). Products in
2 | P a g e
OPEN ACCESS JOURNAL 2021
each category vary in longevity profile, impact, and collection methods, among other
differences.[3] CRTs have a relatively high concentration of lead and phosphors (not to be
confused with phosphorus), both of which are necessary for the display. The United States
Environmental Protection Agency (EPA) includes discarded CRT monitors in its category of
"hazardous household waste"[4] but considers CRTs that have been set aside for testing to be
commodities if they are not discarded, speculatively accumulated, or left unprotected from
weather and other damage. These CRT devices are often confused between the DLP Rear
Projection TV, both of which have a different recycling process due to the materials of which
they are composed. The EU and its member states operate a system via the European Waste
Catalogue (EWC) - a European Council Directive, which is interpreted into "member state
law". In the UK, this is in the form of the List of Wastes Directive. However, the list (and
EWC) gives a broad definition (EWC Code 16 02 13*) of what is hazardous electronic waste,
requiring "waste operators" to employ the Hazardous Waste Regulations (Annex 1A, Annex
1B) for refined definition. Constituent materials in the waste also require assessment via the
combination of Annex II and Annex III, again allowing operators to further determine whether
a waste is hazardous.[5] Debate continues over the distinction between "commodity" and
"waste" electronics definitions. Some exporters are accused of deliberately leaving difficult-
to-recycle, obsolete, or non-repairable equipment mixed in loads of working equipment
(though this may also come through ignorance, or to avoid more costly treatment processes).
Protectionists may broaden the definition of "waste" electronics in order to protect domestic
markets from working secondary equipment. The high value of the computer recycling subset
of electronic waste (working and reusable laptops, desktops, and components like RAM) can
help pay the cost of transportation for a larger number of worthless pieces than what can be
achieved with display devices, which have less (or negative) scrap value. In A 2011 report,
"Ghana E-Waste Country Assessment",[6] found that of 215,000 tons of electronics imported
to Ghana, 30% were brand new and 70% were used. Of the used product, the study concluded
that 15% was not reused and was scrapped or discarded. This contrasts with published but
uncredited claims that 80% of the imports into Ghana were being burned in primitive
conditions.
Human health and safety
Residents living near the recycling sites
3 | P a g e
OPEN ACCESS JOURNAL 2021
Residents living around the e-waste recycling sites, even if they do not involve in e-waste
recycling activities, can also face the environmental exposure due to the food, water, and
environmental contamination caused by e-waste, because they can easily contact to e-waste
contaminated air, water, soil, dust, and food sources. In general, there are three main exposure
pathways: inhalation, ingestion, and dermal contact.[121]
Studies show that people living around e-waste recycling sites have a higher daily intake of
heavy metals and a more serious body burden. Potential health risks include mental health,
impaired cognitive function, and general physical health damage.[122](See also Electronic
waste#Hazardous) DNA damage was also found more prevalent in all the e-waste exposed
populations (i.e. adults, children, and neonates) than the populations in the control area.[122]
DNA breaks can increase the likelihood of wrong replication and thus mutation, as well as lead
to cancer if the damage is to a tumor suppressor gene .[113]
Prenatal exposure and neonates' health
Prenatal exposure to e-waste has found to have adverse effects on human body burden of
pollutants of the neonates. In Guiyu, one of the most famous e-waste recycling sites in China,
it was found that increased cord blood lead concentration of neonates was associated with
parents' participation in e-waste recycling processes, as well as how long the mothers spent
living in Guiyu and in e-waste recycling factories or workshops during pregnancy.[121]
Besides, a higher placental metallothionein (a small protein marking the exposure of toxic
metals) was found among neonates from Guiyu as a result of Cd exposure, while the higher Cd
level in Guiyu's neonates was related to the involvement in e-waste recycling of their
parents.[123] High PFOA exposure of mothers in Guiyu is related to adverse effect on growth
of their new-born and the prepotency in this area.[124]
Prenatal exposure to informal e-waste recycling can also lead to several adverse birth outcomes
(still birth, low birth weight, low Apgar scores, etc.) and longterm effects such as behavioral
and learning problems of the neonates in their future life.[125]
4 | P a g e
OPEN ACCESS JOURNAL 2021
Children
Children are especially sensitive to e-waste exposure because of several reasons, such as their
smaller size, higher metabolism rate, larger surface area in relation to their weight, and multiple
exposure pathways (for example, dermal, hand-to-mouth, and take-home exposure).[126][122]
They were measured to have an 8-time potential health risk compared to the adult e-waste
recycling workers.[122] Studies have found significant higher blood lead levels (BLL) and
blood cadmium levels (BCL) of children living in e-waste recycling area compared to those
living in control area.[127][128] For example, one study found that the average BLL in Guiyu
was nearly 1.5 times compared to that in the control site (15.3 ug/dL compared to 9.9
ug/dL),[127] while the CDC of the United States has set a reference level for blood lead at 5
ug/dL.[129] The highest concentrations of lead were found in the children of parents whose
workshop dealt with circuit boards and the lowest was among those who recycled plastic.[127]
Exposure to e-waste can cause serious health problems to children. Children's exposure to
developmental neurotoxins containing in e-waste such as lead, mercury, cadmium, chromium
and PBDEs can lead to a higher risk of lower IQ, impaired cognitive function, and other adverse
effects.[130] In certain age groups, a decreased lung function of children in e-waste recycling
sites has been found.[121] Some studies also found associations between children's e-waste
exposure and impaired coagulation,[131] hearing loss,[132] and decreased vaccine antibody
tilters[133] in e-waste recycling area.
E-waste recycling workers
The complex composition and improper handling of e-waste adversely affect human health. A
growing body of epidemiological and clinical evidence has led to increased concern about the
potential threat of e-waste to human health, especially in developing countries such as India
and China. For instance, in terms of health hazards, open burning of printed wiring boards
increases the concentration of dioxins in the surrounding areas. These toxins cause an increased
risk of cancer if inhaled by workers and local residents. Toxic metals and poison can also enter
the bloodstream during the manual extraction and collection of tiny quantities of precious
metals, and workers are continuously exposed to poisonous chemicals and fumes of highly
concentrated acids. Recovering resalable copper by burning insulated wires causes
neurological disorders, and acute exposure to cadmium, found in semiconductors and chip
resistors, can damage the kidneys and liver and cause bone loss. Long-term exposure to lead
5 | P a g e
OPEN ACCESS JOURNAL 2021
on printed circuit boards and computer and television screens can damage the central and
peripheral nervous system and kidneys, and children are more susceptible to these harmful
effects.[134]
The Occupational Safety & Health Administration (OSHA) has summarized several potential
safety hazards of recycling workers in general, such as crushing hazards, hazardous energy
released, and toxic metals.
References:
[1] Raju, R.D., 2021. Waste Management in India – An Overview. United International
Journal for Research & Technology (UIJRT), 2(7), pp.175-196.
https://uijrt.com/articles/v2/i7/UIJRTV2I70022.pdf
[2] Jagadish, P., Anand, R., Mercylona, M.M., Aishwarya, M. and Karki, N., 2021.
Nitrogen Deficiency Detection in Paddy for Urea Fertilizer Management. United
International Journal for Research & Technology (UIJRT), 2(7), pp.55-57.
https://uijrt.com/articles/v2/i7/UIJRTV2I70009.pdf
[3] Behera, G.R., Babu, D.A. and Patil, P.N., 2021. A Review on Design of an Electric
Trolley. United International Journal for Research & Technology (UIJRT), 2(7),
pp.108-111. https://uijrt.com/articles/v2/i7/UIJRTV2I70015.pdf
[4] Toro, M.L., Muhammad, N.A., Shu’aibu, A.R., Garba, M.A., Abdulaziz, A. and Musa,
K., 2021. Security, Privacy Issues and Solutions of Mobile Cloud Computing. United
International Journal for Research & Technology (UIJRT), 2(7), pp.112-117.
https://uijrt.com/articles/v2/i7/UIJRTV2I70016.pdf
[5] Claveria, S.J.D. and Mendoza, F.E., 2021. Micro Food Enterprise in Sorsogon City: An
Assessment. United International Journal for Research & Technology (UIJRT), 2(7),
pp.225-233. https://uijrt.com/articles/v2/i7/UIJRTV2I70028.pdf

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All About E-Waste Management In The World

  • 1. 1 | P a g e OPEN ACCESS JOURNAL 2021 All About E-Waste Management in the World Prof Alex Walter, USA Abstract- Electronic waste or e-waste describes discarded electrical or electronic devices. Used electronics which are destined for refurbishment, reuse, resale, salvage recycling through material recovery, or disposal are also considered e-waste. Informal processing of e-waste in developing countries can lead to adverse human health effects and environmental pollution. Electronic scrap components, such as CPUs, contain potentially harmful materials such as lead, cadmium, beryllium, or brominated flame retardants. Recycling and disposal of e-waste may involve significant risk to health of workers and their communities. Keywords- e-waste, waste, management. Introduction E-waste or electronic waste is created when an electronic product is discarded after the end of its useful life. The rapid expansion of technology and the consumption driven society results in the creation of a very large amount of e-waste. The European Waste Electrical and Electronic Equipment Directive Directive classifies waste in ten categories: Large household appliances (including cooling and freezing appliances), Small household appliances, IT equipment (including monitors), Consumer electronics (including TVs), Lamps and Luminaires, Toys, Tools, Medical devices, Monitoring and control instruments and Automatic dispensers. These include used electronics which are destined for reuse, resale, salvage, recycling, or disposal as well as re-usables (working and repairable electronics) and secondary raw materials (copper, steel, plastic, etc.). The term "waste" is reserved for residue or material which is dumped by the buyer rather than recycled, including residue from reuse and recycling operations, because loads of surplus electronics are frequently commingled (good, recyclable, and non-recyclable). Several public policy advocates apply the term "e-waste" and "e-scrap" broadly to all surplus electronics. Cathode ray tubes (CRTs) are considered one of the hardest types to recycle.[2] On the other hand, the Partnership on Measuring ICT for Development defines e-waste into six categories, namely : (1) Temperature exchange equipment (e.g., air conditioners, freezers), (2) Screens, monitors (e.g., TV, laptop), (3) Lamps(e.g., LED lamps), (4) Large equipment (e.g., washing machines, electric stoves), (5) Small equipment (e.g., microwave, electric shaver), and (6) Small IT and telecommunication equipment (e.g., mobile phones, printers). Products in
  • 2. 2 | P a g e OPEN ACCESS JOURNAL 2021 each category vary in longevity profile, impact, and collection methods, among other differences.[3] CRTs have a relatively high concentration of lead and phosphors (not to be confused with phosphorus), both of which are necessary for the display. The United States Environmental Protection Agency (EPA) includes discarded CRT monitors in its category of "hazardous household waste"[4] but considers CRTs that have been set aside for testing to be commodities if they are not discarded, speculatively accumulated, or left unprotected from weather and other damage. These CRT devices are often confused between the DLP Rear Projection TV, both of which have a different recycling process due to the materials of which they are composed. The EU and its member states operate a system via the European Waste Catalogue (EWC) - a European Council Directive, which is interpreted into "member state law". In the UK, this is in the form of the List of Wastes Directive. However, the list (and EWC) gives a broad definition (EWC Code 16 02 13*) of what is hazardous electronic waste, requiring "waste operators" to employ the Hazardous Waste Regulations (Annex 1A, Annex 1B) for refined definition. Constituent materials in the waste also require assessment via the combination of Annex II and Annex III, again allowing operators to further determine whether a waste is hazardous.[5] Debate continues over the distinction between "commodity" and "waste" electronics definitions. Some exporters are accused of deliberately leaving difficult- to-recycle, obsolete, or non-repairable equipment mixed in loads of working equipment (though this may also come through ignorance, or to avoid more costly treatment processes). Protectionists may broaden the definition of "waste" electronics in order to protect domestic markets from working secondary equipment. The high value of the computer recycling subset of electronic waste (working and reusable laptops, desktops, and components like RAM) can help pay the cost of transportation for a larger number of worthless pieces than what can be achieved with display devices, which have less (or negative) scrap value. In A 2011 report, "Ghana E-Waste Country Assessment",[6] found that of 215,000 tons of electronics imported to Ghana, 30% were brand new and 70% were used. Of the used product, the study concluded that 15% was not reused and was scrapped or discarded. This contrasts with published but uncredited claims that 80% of the imports into Ghana were being burned in primitive conditions. Human health and safety Residents living near the recycling sites
  • 3. 3 | P a g e OPEN ACCESS JOURNAL 2021 Residents living around the e-waste recycling sites, even if they do not involve in e-waste recycling activities, can also face the environmental exposure due to the food, water, and environmental contamination caused by e-waste, because they can easily contact to e-waste contaminated air, water, soil, dust, and food sources. In general, there are three main exposure pathways: inhalation, ingestion, and dermal contact.[121] Studies show that people living around e-waste recycling sites have a higher daily intake of heavy metals and a more serious body burden. Potential health risks include mental health, impaired cognitive function, and general physical health damage.[122](See also Electronic waste#Hazardous) DNA damage was also found more prevalent in all the e-waste exposed populations (i.e. adults, children, and neonates) than the populations in the control area.[122] DNA breaks can increase the likelihood of wrong replication and thus mutation, as well as lead to cancer if the damage is to a tumor suppressor gene .[113] Prenatal exposure and neonates' health Prenatal exposure to e-waste has found to have adverse effects on human body burden of pollutants of the neonates. In Guiyu, one of the most famous e-waste recycling sites in China, it was found that increased cord blood lead concentration of neonates was associated with parents' participation in e-waste recycling processes, as well as how long the mothers spent living in Guiyu and in e-waste recycling factories or workshops during pregnancy.[121] Besides, a higher placental metallothionein (a small protein marking the exposure of toxic metals) was found among neonates from Guiyu as a result of Cd exposure, while the higher Cd level in Guiyu's neonates was related to the involvement in e-waste recycling of their parents.[123] High PFOA exposure of mothers in Guiyu is related to adverse effect on growth of their new-born and the prepotency in this area.[124] Prenatal exposure to informal e-waste recycling can also lead to several adverse birth outcomes (still birth, low birth weight, low Apgar scores, etc.) and longterm effects such as behavioral and learning problems of the neonates in their future life.[125]
  • 4. 4 | P a g e OPEN ACCESS JOURNAL 2021 Children Children are especially sensitive to e-waste exposure because of several reasons, such as their smaller size, higher metabolism rate, larger surface area in relation to their weight, and multiple exposure pathways (for example, dermal, hand-to-mouth, and take-home exposure).[126][122] They were measured to have an 8-time potential health risk compared to the adult e-waste recycling workers.[122] Studies have found significant higher blood lead levels (BLL) and blood cadmium levels (BCL) of children living in e-waste recycling area compared to those living in control area.[127][128] For example, one study found that the average BLL in Guiyu was nearly 1.5 times compared to that in the control site (15.3 ug/dL compared to 9.9 ug/dL),[127] while the CDC of the United States has set a reference level for blood lead at 5 ug/dL.[129] The highest concentrations of lead were found in the children of parents whose workshop dealt with circuit boards and the lowest was among those who recycled plastic.[127] Exposure to e-waste can cause serious health problems to children. Children's exposure to developmental neurotoxins containing in e-waste such as lead, mercury, cadmium, chromium and PBDEs can lead to a higher risk of lower IQ, impaired cognitive function, and other adverse effects.[130] In certain age groups, a decreased lung function of children in e-waste recycling sites has been found.[121] Some studies also found associations between children's e-waste exposure and impaired coagulation,[131] hearing loss,[132] and decreased vaccine antibody tilters[133] in e-waste recycling area. E-waste recycling workers The complex composition and improper handling of e-waste adversely affect human health. A growing body of epidemiological and clinical evidence has led to increased concern about the potential threat of e-waste to human health, especially in developing countries such as India and China. For instance, in terms of health hazards, open burning of printed wiring boards increases the concentration of dioxins in the surrounding areas. These toxins cause an increased risk of cancer if inhaled by workers and local residents. Toxic metals and poison can also enter the bloodstream during the manual extraction and collection of tiny quantities of precious metals, and workers are continuously exposed to poisonous chemicals and fumes of highly concentrated acids. Recovering resalable copper by burning insulated wires causes neurological disorders, and acute exposure to cadmium, found in semiconductors and chip resistors, can damage the kidneys and liver and cause bone loss. Long-term exposure to lead
  • 5. 5 | P a g e OPEN ACCESS JOURNAL 2021 on printed circuit boards and computer and television screens can damage the central and peripheral nervous system and kidneys, and children are more susceptible to these harmful effects.[134] The Occupational Safety & Health Administration (OSHA) has summarized several potential safety hazards of recycling workers in general, such as crushing hazards, hazardous energy released, and toxic metals. References: [1] Raju, R.D., 2021. Waste Management in India – An Overview. United International Journal for Research & Technology (UIJRT), 2(7), pp.175-196. https://uijrt.com/articles/v2/i7/UIJRTV2I70022.pdf [2] Jagadish, P., Anand, R., Mercylona, M.M., Aishwarya, M. and Karki, N., 2021. Nitrogen Deficiency Detection in Paddy for Urea Fertilizer Management. United International Journal for Research & Technology (UIJRT), 2(7), pp.55-57. https://uijrt.com/articles/v2/i7/UIJRTV2I70009.pdf [3] Behera, G.R., Babu, D.A. and Patil, P.N., 2021. A Review on Design of an Electric Trolley. United International Journal for Research & Technology (UIJRT), 2(7), pp.108-111. https://uijrt.com/articles/v2/i7/UIJRTV2I70015.pdf [4] Toro, M.L., Muhammad, N.A., Shu’aibu, A.R., Garba, M.A., Abdulaziz, A. and Musa, K., 2021. Security, Privacy Issues and Solutions of Mobile Cloud Computing. United International Journal for Research & Technology (UIJRT), 2(7), pp.112-117. https://uijrt.com/articles/v2/i7/UIJRTV2I70016.pdf [5] Claveria, S.J.D. and Mendoza, F.E., 2021. Micro Food Enterprise in Sorsogon City: An Assessment. United International Journal for Research & Technology (UIJRT), 2(7), pp.225-233. https://uijrt.com/articles/v2/i7/UIJRTV2I70028.pdf