Personal tools
WEEEPositionPaper.html
Home
About |
Working Groups
Publications |
Join Events |
Topics Chapters |
News
Search |
Computer Professionals for Social Responsibility |
Working Group on Computing and the Environment (WGCE)
Computer Professionals for Social Responsibility (CPSR)
The significance of this technological abundance can been seen in the recent uproar caused by the Y2K problem. The total cost associated with solving the Y2K problem is equivalent to that of the Apollo space program. Its estimated that the cost within the United States exceeded $500 billion, while the European Union members spent about $210 billion.
Looking more specifically at computer technology, the degree of economic impact of technology growth is indicated by the companies that operate in the arena. Firms such as Microsoft, Intel, IBM, Lucent, AT&T are near or at the top ranks of corporate growth and significance. According to the U.S. Department of Commerce, the "Electronic and other electric equipment" segment of the economy represents 261.2 billion dollars in 1997, almost 2% of the US economy.
Concurrent to the growth in the use and production of technology, of course, has been the growth in the need to dispose of obsolete and broken equipment. In 1995, there were over 21,000,000 personal computers sold in the United States. When one understands that a majority of these will become obsolete within 2 years and that the number sold is increasing, one can get some idea of the impact of the waste stream that these discarded computers represent. A 1991 study at Carnegie-Mellon University estimated that 150 million personal computers would require disposal by the year 2005. A subsequent study in 1997 modified this estimate down to 55 million, but also estimates that the equivalent of 15 million additional PCs in unwanted parts would be deposited in landfills. Disposal of this equipment would require approximately an acre of land piled four thousand feet tall in waste.
The two common means of dealing with discarded and broken electronic goods are deposit in landfills and incineration. In landfills, the toxic chemicals contained in electronic goods will over time leach into the groundwater flow and eventually into the human food chain and drinking water supply. Incineration releases these toxic chemicals directly into the air, where they are adsorbed by humans during respiration. Incineration also creates ash and slag containing toxic chemicals, which also require disposal. The lack of recycling and reuse of electronic goods also creates a need for new raw materials and therefore is a secondary cause of the pollution generated in mining and processing of these materials.
Characteristic of Electronic Waste
Appendix I shows the typical contents of a personal computer, and to what extent they are recyclable. The waste resultant from the disposal of electronics is an amalgamation of solid and hazardous waste that poses a difficult set of problems. These problems are caused by the complex nature of the equipment and the nature of the components within the waste. Among the materials that compose this waste are:
- assorted plastics
- chromium
- lead
- mercury
- various heavy metals
Extended Product Responsibility
Extended product responsibility (EPR) embodies an emerging principle of pollution prevention policies that focuses on the life-cycle concept of a product, and that identifies opportunities to prevent pollution and reduce energy consumption throughout the product's life. Included in this concept is the extension of the responsibility of producers to include involvement in take-back schemes in order to ensure the recycling of products and the active involvement of producers in the post-consumer stage of product life-cycle.
The purpose of the ERP initiative is to find ways for the producers of waste to be responsible for its disposal at the end of its life span. This entails several benefits, including:
- The waste is accounted for at its end of life
- There is a market for this waste
- The waste does not become unmarked hazardous waste within waste processing facilities, posing a significant risk to the health and welfare of those in proximity of these facilities.
EPR includes several different objectives:
- physical responsibility for products
- A producer is responsible for the physical management
of the products, used products, and the impacts of the products through
the development of technology or provision of services to manage the product
after its life cycle is complete.
- economic responsibility
- A producer must cover all or part of the costs for managing
wastes at the end of a product's life (eg. collection, processing, treatment
or disposal).
- liability
- The producer of a product assumes responsibility for
environmental damage caused by the production, use, or disposal of a product.
- informative liability
- The producer is required to provide information on the
product and its effects during various stages of its life cycle.
History of EPR
There have been significant developments toward implementing EPR in the last decade, including new EPR-related laws in German, Netherlands, Norway, Switzerland, and Denmark.
Germany
Most agree that the first major step towards advancing EPR was the 1991 German "Ordinance on Avoidance of Packaging Waste". This ordinance requires industry to take back, reuse, and/or recycle packaging materials. This shifts the burden of waste management from the municipal authorities to the manufacturers, distributors and retailers who generate waste.
This law was implemented without the German government dictating any specific changes, but relied upon industry to find an efficient manner to implement ERP. This was accomplished when German industry formed the Duales System Deutschland (DSD). This private entity collects and processes used packaging, and takes responsibility for each stage of the packaging process. Under the DSD system, manufacturers apply for and pay DSD a fee to place their symbol, a "green dot", on their packages to ensure that DSD will collect and recycle their packaging. Although the DSD is not responsible for the actual recycling, it does approve packaging design, and the green-dot signifies that the packaging will be recycled. This method provides information to the consumer and a funding source for recycling packaging that would otherwise be problematic. As a result of the widespread use of the green dot symbol, a sufficiently large amount of waste is identified to make the recycling economically viable. This approach to ERP forms a successful waste-avoidance system.
In 1994, Germany passed the Eco-Cycle Waste Act, which specified take-back mandates, allowing the government to impose take-back and other obligations on sellers of products. It also encouraged product responsibility on the part of product designers, producers, users, and distributors. This approach has encouraged corporations to design, produce and distribute products with Design for the Environment methodologies that include developing ways to avoid the creation of waste and to recover waste in an environmentally sound manner.
Netherlands
In March 1997, the Netherlands issued a draft entitled "Dutch Decree on Removal of Electronic Appliances". The purpose of this proposal was to require producers and importers of electronic goods to take back products free of charge for disposal or recycling. This essentially allowed a consumer to return old appliances at no extra cost. The products included in the draft decree included are televisions, CD players, computers, copiers, fax/telecommunication machines, as well as domestic products such as washing machines, refrigerators and small appliances.
The decree did not allow the cost of the recycling and disposal to be passed on to the retailers and municipalities, but did allow these costs to be passed on to the consumer. This was done to allow economic choice to decide how the costs would be borne and to place the consumer in the position of defining the proper balance for these costs within the economic system.
The objectives of the WEEE are simple. First, the WEEE seeks to contribute to the protection of human health and the environment by preventing air, water, and soil pollution. Current waste management practices rely upon landfill disposal and, to a lesser extent, incineration of products in question, resulting in the introduction of a variety of hazardous materials into the environment. Second, the WEEE seeks to avoid waste generation and reduce the harmfulness of waste. This is accomplished through requiring recycling and reuse of components where practical, which reduces both pollution resulting from disposal and that resulting from the production of virgin materials.
On essential aspect of the WEEE is a requirement to eliminate or reduce the use of certain harmful substances in affected products. In particular, the WEEE covers the use of lead, mercury, cadmium, and hexavalent chromium. These materials are currently used in a variety of affected products, for example as leaded solder on printed circuit boards, and in various electronic components. There are a variety of health dangers, including damage to various organs and cancer, associated with exposure to these substances, primarily a result of leaching from landfills into water supplies and into the food chain. The WEEE directs member states to establish maximum levels of use for these materials in affected products and it establishes exemptions for those cases in which no practical substitution is available.
The second essential aspect of the WEEE is an increase in producer responsibility for disposal of covered products. Responsibility for disposal of covered products currently rests primarily with municipalities, and these products currently constitute the most rapidly growing segment of municipal waste. This growth is increasing the burden on already overused landfills, and increasing the amount of toxic input to landfills as well. Requiring producers to assume more responsibility for equipment at its end of life cycle will have two benefits. First, it will allow economies of scale to be applied to disposal and recycling operations and will provide product-specific expertise to improve these efforts. Second, it will naturally encourage producers to employ manufacturing techniques that facilitate recycling and that use recycled content.
- The primary expected benefit of the WEEE would be the reduction of pollution that would occur in two different ways. First, the introduction of toxic material into air, water, and soil would be reduced through the reduction of the amount of hazardous material contained in waste equipment sent to landfills and incinerators. Second, the environmental impact of producing new virgin raw materials would be reduced through increased reuse and recycling of equipment at the end of its life cycle.
- As a secondary benefit, the WEEE would be likely to lead to improvements in manufacturing, including a reduction of hazardous materials in workplaces where covered equipment is produced and a cost savings resulting from the reuse of obsolete components. This benefit would have an impact broader than the European market as well as the electronics industry becomes familiar with responsible manufacturing techniques.
- Other secondary benefits of the WEEE include reduced cost of waste collection and disposal for municipalities and the creation of jobs in the recycling industry.
- The estimated costs of the WEEE are minimal. The EU estimates an average impact on costs for covered equipment on the order of 1%. This cost increase is likely to be temporary, however, as producers improve the efficiency of products with regards to reuse and recovery of components.
- The WEEE is feasible. Substitutes for the materials subject to being eliminated under the WEEE are now available. In the few cases where replacement of hazardous substances would be difficult or unduly expensive, exceptions have been written into the WEEE. Recycling will require an initial investment and effort to establish, but there is no technical obstacle to this part of the WEEE.
- The WEEE is acceptable under current international trade laws. The GATT article XX and the TBT agreement both recognize the right to implement measures "necessary to protect human, animal or plant life or health". The WEEE clearly falls into this category and it does not discriminate in any way between domestic and foreign manufacturers.
- The WEEE is supported by US and European environmental groups. In the US, the WEEE has the support of the Silicon Valley Toxics Coalition (www.svtc.org), a recognized proponent of environmental consciousness in the electronics industry. In Europe, the WEEE is strongly supported by the European Environmental Bureau (www.eeb.org), a consortium of many European environmental organizations.
|
(in lbs) |
|
Contents |
Monitor | |||
0.1900
|
3.8000
|
|
metal joining, radiation shield/CRT, PWB |
9.8400
|
12.3000
|
|
structural, magnetivity/(steel) housing, CRT, PWB |
0.4200
|
0.6000
|
|
metal joining/PWB, CRT |
6.8000
|
8.5000
|
|
structural, conductivity/housing, CRT, PWB, connectors |
3.7800
|
4.2000
|
|
Conductivity/CRT, PWB, connectors |
0.0000
|
0.1000
|
|
in vacuum tube/CRT |
0.4080
|
0.5100
|
|
structural, magnetivity/(steel) housing, CRT, PWB |
0.7920
|
1.3200
|
|
battery, phosphor emitter/PWB, CRT |
0.0000
|
0.1000
|
|
red phosphor emitter/CRT |
0.0000
|
0.0000
|
|
green phosphor activator, dopant/CRT, PWB |
0.0000
|
0.1000
|
|
red phosphor emitter/CRT |
0.0000
|
0.1000
|
|
phosphor activator/PWB |
0.0850
|
0.1000
|
|
structural, magnetivity/(steel) housing, CRT, PWB |
0.0000
|
0.1000
|
|
structural, magnetivity/(steel) housing, CRT, PWB |
0.0000
|
0.1000
|
|
diodes/housing, PWB, CRT |
0.0000
|
0.1000
|
|
battery, glu-green phosphor emitter/housing, PWB, CRT |
0.0000
|
15.0000
|
|
glass, solid state devices/CRT,PWB |
22.3150
|
47.0300
|
Total for Monitor | |
Computer | |||
2.7600
|
13.8000
|
|
includes organics, oxides other than silica |
0.0000
|
0.1000
|
|
Semiconductor/PWB |
0.0000
|
0.1000
|
|
Semiconductor/PWB |
0.0000
|
0.1000
|
|
Capacitors/PWB, power supply |
0.0600
|
0.1000
|
|
transistor, rectifiers/PWB |
0.0000
|
0.1000
|
|
thermal conductivity/PWB, connectors |
0.0990
|
0.1000
|
|
Connectivity, conductivity/PWB, connectors |
0.0000
|
0.1000
|
|
pigment, alloying agent/(aluminum) housing |
0.0800
|
0.1000
|
|
resistive circuit/PWB |
0.0950
|
0.1000
|
|
Connectivity, conductivity/PWB, connectors |
0.0980
|
0.1000
|
|
Conductivity/PWB, connectors |
0.0000
|
0.1000
|
|
wetting agent in thick film/PWB |
0.0000
|
0.1000
|
|
Decorative, hardener/(steel) housing |
0.0007
|
0.0010
|
|
rectifiers/PWB |
0.0000
|
0.1000
|
|
welding allow/housing |
0.0500
|
0.1000
|
|
thick film conductor/PWB |
0.0950
|
0.1000
|
|
thick film conductor/PWB |
0.0000
|
0.1000
|
|
batteries, switches/housing, PWB |
0.0000
|
0.1000
|
|
doping agents in transistors/PWB |
3.3377
|
15.5010
|
Total for computer | |
25.6527
|
78.0319
|
Total for computer and monitor |
Created before October 2004