Sustainable product prototyping - The REDI Project
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The REDI Project

 

The Regional Eco-efficiency Demonstrator Initiative (REDI) was launched in late 1995 to show how eco-efficiency and commercial viability could be aligned within new product designs. A wide range of companies has been involved, reflecting the supply-chain and whole-life orientations of the project. Funding has been received from the Esme Fairburn Charitable Trust and the European Commission, as well as from companies and business support organizations.

 

A major deliverable from REDI is a software tool which aims to assist the designer to minimize ‘end of life’ liabilities and maximize whole-life value in a number of ways. Firstly, by entering the product specifications into the software tool, the designer is warned of any potentially hazardous materials included, wherever they may be located within the product. This all flows at the very least, for the designer to be aware of the liabilities in the product and to quantify them for further reference. This information can then be used within scenarios, to identify vulnerability of particular designs to future regulatory developments.

 

Secondly, by tracking the value throughout product life, REDI gives the user a snapshot of the ‘value-adding’ and ‘value-reducing’ processes throughout the product’s life, tracking material fluxes from raw resources to finished products and waste streams. A key element of this functionality is the ability to

 

Representation of product life cycle within REDI

model the scrap and waste rates of the various process flows that the product undergoes and also to estimate overall material recovery percentages.

Each stage of the life-cycle, from component manufacture to waste processing, is modeled; each draws on material/energy resources, and each creates waste. These fluxes of material flows are modeled so that resource and waste burdens can be calculated for each unit of output from the production process.

 

The concept of eco-efficiency is central to the REDI design tool. Eco-efficiency is a measure of how much customer value is offered by the product compared with the resources needed to create that value. By modeling value-adding and value-reducing processes throughout the product’s life, its overall eco-efficiency can be derived, in the form of an eco-efficiency index. Designers can use this index to explore the optimization of eco-efficiency at an early stage of product design. This is a novel aspect of design tools, and an important function of the REDI project is to appraise how useful this eco-efficiency approach could be in a commercial design context.

 

One of the major uses of the REDI tool will be the management, and ‘designing out’, of liabilities resulting from the product’s ‘end of life’ and manufacturing phases. It is recognized that small firms have an important role in achieving a more eco-efficient industrial base. Yet many recent initiatives (e.g. waste minimization) have encountered difficulties in attracting small firms. Therefore REDI has been constructed to allow an easy entry route for small firms.

 

The design tool has initially focused on the electronic equipment sector, working closely with a range of leading companies including Hewlett-Packard, Rank Xerox, NCR, Telecom Sciences and the Scottish Electronics Forum. It is intended to extend the application of the tool to other sectors once the approach has been validated for electronic equipment.

 

Whole-life liability management

 

One of the major uses of the REDI tool will be the management, and ‘designing out’, of liabilities resulting from the product’s ‘end of life’ and manufacturing phases. Many of these liabilities are hidden costs falling outside the conventional design brief (i.e. the cost of complying with Control of Substances Hazardous to Health (COSHH) regulations due to the use of particular solvents during manufacture).

 

Of particular significance is the cost of producing, handling and disposing of packaging used to ship components and assemblies from supplier to manufacturer. These costs are rarely considered in product engineering, but they can end up being substantial. It is only by tracking all such packaging throughout the life-cycle that it is possible to quantify the cost, and thereby to focus management attention on reducing cost.

 

In addition, it is important to ensure that designers are aware of all hazardous materials used in the product, particularly if these end up being shipped in the product where they can contaminate otherwise recoverable resources at ‘end of life’. This is presently extremely difficult, for two reasons:

 

• product designers do not usually possess information on material composition of bought-in components nor are they usually fully aware of regulatory constraints affecting the use and disposal of different materials.

The REDI tool addresses these needs, making information available in a form which is valuable to small and large firms. It achieves that by incorporating within the tool two databases. One is a component database which contains information on common components used in electronic equipment. Initially a demonstration component database has been created, covering a limited range of components, to allow the tool to be used and evaluated.

 

The second database contains information on materials and regulations pertaining to those materials. This data resource all flows REDI to flag up potential hazards, without getting bogged down in details of environmental regulations. However it will be possible to link REDI to one of a typical product.

The proprietary environmental databases to access more detailed information.

 

Whole-life value management

 

As already mentioned, the ability to optimize ‘value-added’ against

resource utilization is essential to develop eco-efficient products. REDI achieves this by calculating the embedded value in a product at every stage in its life.

This shows a modest raw materials value (£B) rising through the manufacturing processes to a maximum value at the point of sale (£A). As the product is used, it steadily loses value (ignoring some discontinuities due to maintenance and repair) until it finishes up in, say, a municipal waste site. Here it has a negative value since it requires some waste processing and its materials are not yet available for reuse.

 

At this stage, the product can either by treated by a recovery system which releases its intrinsic value, and brings the net value back up (£C); or it can be disposed of without recovery of its intrinsic resources, incurring a further loss of value (£C’).

Based on information from recycling plants, the designer can input recovery rates and costs for the product and its constituents. This all flows REDI to create the value profile, whereupon the designer can explore how design decisions affect the profile. In the case of a

poorly designed product, where the ‘end of life’ processing costs are high, it may not be possible to achieve a positive ‘value added’ by any ‘end of life’ process. In such a case, the fate of the product will be governed by regulatory constraints rather than by commercial judgment.

 

Eco-efficiency index

 

The index is computed as the ratio between maximum product value (in the above case £A) and the net whole-life material value consumed in achieving that product value (£B less £C). That is: heco = A/(B–C)

The index is a convenient way of summarizing the eco-efficiency performance of a design. It assumes that the value at point of sale (A) can be taken as the price a consumer is prepared to pay to acquire the product, i.e. its retail price. Material values B & C can be computed by the REDI model: clearly, designs which improve the net value of resources extracted from product (C), and/or which reduce the resources consumed in manufacture (B), will attract an improved eco-efficiency index.

 

Maximizing impact

 

The next stage in the project will address the evaluation of the REDI tool. Participating companies will be given an opportunity to experiment with the tool, to apply it to product design situations relevant to their own businesses.

It is important to get feedback from smaller firms at this stage, so the project is working with various organizations.

 

The tool is structured on economic factors, since these will drive moves towards eco-efficient products in the commercial world.

interests of small and medium enterprises.

 

Using the design tool

 

In order to maximize the value of REDI, considerable effort has gone into the user interface. The tool is coded in Microsoft Access with Visual Basic controls, offering an efficient prototyping environment and flexibility to customize the user interface. An example of a screen, showing product information summary, is illustrated.

 

Conclusions

 

The REDI project has successfully developed a design tool which all flows designers to optimize the eco-efficiency of products. At

this stage, it has been focused on electronic equipment, but this applicability can be expanded once the use of the tool has been validated.

 

The design tool is structured around a whole-life representation of material flows required to manufacture, use and dispose of products. Economic values of material flows are built into the tool, since ‘end of life’ processing is dependent upon the intrinsic value of resources embedded within products.

An eco-efficiency index has been proposed, and is built into the tool. The formulation of this index needs to be appraised by designers and engineers.

 

The tool differs from conventional life cycle analysis models, in that it does not attempt to quantify every emission and resource utilization. Instead, it quantifies whole-life material utilization and recovery, and presents this information in a form directly useful to the design process. The tool is also unashamedly structured on economic factors, since these will drive moves towards eco-efficient products in the commercial world.

The next stage in the work seeks to generate feedback on the tool from designers and engineers, in the context of both large and small company environments. Moving companies towards sustainability through eco-design: conditions for success

 

Senior Advisor Environmental Engineering, Environmental Competence Centre, Philips Sound & Vision, the Netherlands

 

Ab Stevels studied Chemistry at the Eindhoven University of Technology and, after being employed at Philips Electronics Eindhoven in 1966, he received his PhD in Physics and Chemistry at the Groningen University, the Netherlands.

In 1969 he joined the Philips Research Laboratories and worked on various subjects in solid state chemistry and materials science. After changing to the Glass division in 1981, he worked in various capacities: glass technologist, laboratory manager, head of prototyping and general manager of the Optics business. In 1989 he was transferred to the Consumer Electronics division (his assignments included the management of the laser optics business and projects in Asia). From January, 1993 he has been senior advisor on environmental engineering of Philips Consumer Electronics and from December 1995 he was appointed part-time professor in Environmental Design at the Faculty of Industrial Design Engineering, the Delft University of Technology, and the Netherlands.

 

Experiences in moving companies towards more sustainability through eco-design are highlighted in this paper. Incremental improvement of environmental product attributes is well underway especially in those areas where eco-design can be linked to cost reductions. More radical re-design of products is currently still hampered by lack of appropriate validation methods. Finding product alternatives and introducing them to the market will require intensive stakeholder dialogue. The formulation of common goals will be crucial to move society towards sustainability.

 

Introduction

 

  he need to achieve sustainable development poses an enormous challenge for society. It is estimated that in order to make this happen, the burden on the environment in industrialized countries will have to be reduced by at least a ‘factor 10’ in fifty years time (Weterings & Opschoor, 1992). Over a shorter time scale Von Weizsacker, Lovins and Lovins (Weizsacker, Lovins & Lovins, 1995) advocate an increase in the eco-efficiency of consumption by a ‘factor 4’. In order to realize this a number of techno-economical, social and ethical issues will have to be tackled. This paper highlights the role of companies in achieving the societal goal of sustainability through eco-design. Basically this is a technical issue; however, this paper will show that mindset and corporate culture are important conditions for success.

The Brundtland Commission report (The Brundtland Commission, 1997) brought the concept of sustainability to the attention of a wide audience. However, in the subsequent years various actors have became more and more involved in the debate. In business the increasing eco-efficiency of production processes has been progressing for several decades; with, the oil price shocks of the early seventies and eighties greatly accelerating efforts. Nowadays the concept of eco-efficiency is well accepted in smart industrial practice; but attention to eco-efficiency of products has evolved only recently.

 

This flows that after the initial awareness phase, national governments in various countries stepped in with (draft) legislation and regulation. Between 1991–1994 the first environmental criteria appeared in consumer product tests and in eco-labels; shortly after this leading companies started to implement product-related eco-design and eco-efficiency considerations. More recently it has been realized that product-based eco-efficiency as such is not good enough to realize breakthrough gains. The systems/infrastructure in which the product functions has to be considered as well.

 

This paper suggests that eco-design has several levels of sophistication. For each of the first three levels, i.e.improvement of current design, radical re-design based on existing product concepts and product alternatives, experience from Philips Sound & Vision (S&V) is described, both in terms of critical success factors and support tools used or needed.

 

Levels in eco-design

 

The eco-design process has been described by Brezet, Cramer and Stevels (Brezet, Cramer & Stevels, 1995) as a staircase with four steps.

 

First step: incremental improvement of products Second step: (complete) re-design of existing product concepts.

 

Third step: alternative fulfilment

of functionality, new concepts Fourth step: functionality concepts completely fitting into the sustainable society.

 

When developing eco-prototyping projects or implementing eco-design in a wider sense in organizations, it is important to know exactly what level of eco-design the company or Business Unit should be aiming for.

 

The choice of the level has far-reaching consequences for the type of information required, type of institution/department involved, the environmental validation (the ‘greeness’ of the result), financial aspects, consumer life style and infrastructure.

 

It can also be concluded from activities on level 1 and level 2 are well within the span of control of individual companies. For success at level 3 and 4, consumer life style and infrastructure changes in society play a major role.

Level 1: eco-design activities, incremental improvement

Level 1 eco-design actions can be carried out by all companies launching products into the market and every employee can contribute to it.

 

Common sense plays an important part in these type of activities. Essentially it is bringing together the following type of information:

 

By counting, i.e.

• how many parts are in the products?

• how many types of material have been used?

• how many screws or other fixtures are in place?

By measuring, i.e.

• energy consumption

• weight

• presence of environmentally relevant substances

• disassembly time of the main parts?

By calculating, i.e.

• what is the cost of environmental improvements?

• what are the yields of environmental improvements?

Bringing together information almost automatically leads to the generation of ‘green’ improvements

   

Philips Environmental Policy Statement

Environmental care is an integral part of the industrial and product policy of Philips.

 

The four basic principles are: • sustainable development • prevention is better than cure • the total effect on the environment counts • open contact with the authorities.

These principles lead to the following policy statement:

• Philips is committed to environmental care in all its operations. All parts of the organization will incorporate this into the management of their activities.

• Philips encourages the assessment of the total environmental impact when introducing new processes, products and packaging.

• Philips recognises the importance of an on-going involvement and commitment of management and of all employees.

• Philips will strive to conduct its industrial and commercial activities in such a way that the quality of the environment now and in the future preserved. Philips supports the Business Charter for Sustainable Development of the International Chamber of Commerce (ICC), dated March 1991.

• Philips is committed to complying with all applicable environmental laws and regulations and emphasises the necessity of international harmonization of environmental regulations.

• Philips will cooperate with governments, regulatory bodies, industries and consumer organizations and will take the initiative, where necessary, to promote workable and improved codes of practice and effective laws and regulations.

          Philips encourages the collection and qualified recycling of products at the end of their useful life by third parties. In this respect, Philips will provide the necessary information concerning its products.

• Philips will strive to inform the customer in such a way that he will be able to take the respective environmental consequences into account in his decision to buy, provided an assessment of the total environmental impact of its products has been made.

Source: Philips Electronic experience has shown that the process of bringing together information, as described above, almost automatically leads to the generation of ‘green’ improvements (and also leads to improvements outside the strict environmental area). The reason for this is due to the complexity of today’s products and because most companies are still organized into specialized departments focusing on particular parts of the total product concept (i.e.mechanical, electrical, electronic, manufacturing planning, etc). Eco-design is essentially a cross-functional activity!

In order to successfully integrate level 1 eco-design activities, basically four types of action are needed:

 

• formulation of the environmental vision, policy and overall targets by management.

• incorporation of an environmental section into the individual product specification.

• eco-design training and the publication of an environmental design manual with mandatory design rules, directives and recom-mendations, background knowledge on how to successfully execute eco-design

• follow-up both at management level (‘review’) and in the product creation process (environmental release).

In order for an organization to start operating in this way, a business rationale must be developed, technical matters should be addressed and environmental awareness should be generated.

   

Environmental Design Manual    

Philips Electronics N.V. 1996

Part 1: Sound & Vision (S&V),

Business Electronics (BE) and

Communication Systems (CS)

environmental requirements

• how to use the manual

• summary of mandatory

design rules

• environmental weight

and calculation method

• marking and labelling

of mechanical parts

• packaging

• customer information

• purchasing directives

• banned Substances

• batteries

• ozone depleting chemicals

 

The business rationale for level 1 eco-design activities is primarily based on compliance with legislation/regulation and to changes where eco-design and cost reduction are directly linked, such as product weight and packaging weight reduction, reduction of (dis)assembly time, reduction of wiring/cabling and the application of recycled material. Experience indicates that successful eco-design generates environmental improvements and cost reduction, which contradicts the well-established prejudice that ‘ the environment’ only costs money. It is more difficult to derive market advantages from level 1 eco-design activities; as, both private and original equipment manu-facturers (OEM) customers Part 2: Business group specific environmental standards.

 

Part 3: Environmental policy:

 

S&V, BE and CS environmental organization environmental recommendations and information

• chemical content

• power consumption

• end-of-life costs & design

recommendations

• environmental management

systems

• LCA/Eco-indicator

• eco labels

simply expect that quality companies continuously introduce environmental improvements in their new product generations. Moreover, level 1 eco-design improvements are straightforward and easy for competitors to follow, so commercial advantages will be short-lived.

Philips Sound & Vision (S&V) has approached eco-design activities both through a ‘top-down’ and a ‘bottom-up’ approach. The ‘top-down’ approach was launched through the formulation of a vision/policy statement in 1991. This was followed by the implementation of an environmental program called ‘The Environmental Opportunity’. On a company-wide basis the following three goals are set:

• certification according to ISO

Part 4: Annexes environmental release status of:

 

            passive components

            active components

            electromechanical components

            key components

            laminates (for PWBs)

            plastics

            metals

            chemicals

Philips CE list of environmentally relevant substances • summary of legislation and regulations.

• 15% packaging reduction in all operations by the year 2000.

Each Business Unit has to establish a program addressing:

• eco-design energy consumption of products

                 

The need to drastically improve the eco-efficiency of products and services through level 3 eco-design also calls for an intense stakeholder dialogue.

and training programs. The Environmental Design Manual gives the mandatory design rules (to be checked at product release), design directives and design recommendations. The supporting text and information tables are organized in such a way that they not only invite the designers/developers to fulfil the requirements, but also to surpass this minimum as much as possible (see JSPD, Issue 1, p. 7).

Training programs include the following items:

 

 introduction

 

What is eco-design environmental product analysis ?

 

Environmental validation

 

How to environmentally improve energy consumption materials application

chemical content packaging ‘end of life’ properties • ISO 14001 • business and environment eco-design as business issue

environmental business analysis/roadmaps

green consumer behavior

environmental product strategy • legal and political issues

 

• implementation of eco-design • ‘end of life’/recycling specials.

Level 2: eco-design activities, radical re-design based on existing concepts.

In level 2 eco-design activities existing product concepts are environmentally improved up to the limits which physics, chemistry and electronics will allow. This is difficult to achieve

through a ‘Plan-Do-Check-Action’ approach. Therefore level 2 eco-design projects are being organized in pre-prototyping or research laboratories.

Going for the limits for energy consumption, materials application and ‘end of life’/durability of a single product always implies compromises and ‘tradeoffs’ as to what is the best or the better environmental option. Drastically improving one item (i.e. energy consumption) can have negative implications for other items, such as materials or ‘end of life’. Therefore level 2 activities require environmental validation; Life Cycle Assessment (eco-indicator calculations) and Life Cycle Cost calculations are needed to track down the best options, with commonsense and the checklist-based activities of level 1 – no longer applicable to a higher level of sophisication.

In order to find out what the best approach for radical re-design in an industrial setting would be, the S&V Business Unit has organized a ‘Green TV’ project. In this project attention has been focussed on both the technical issues, and corporate culture issues, like how to overcome barriers and prejudice and how to simulate green creativity. The experience in this project has shown that it is very beneficial to allow ‘open thinking’ in the first stage of the project. This means that the normal boundary conditions of an industrial project, quality, cost price and throughput time, are set aside for a certain period of time. Later on these are brought in again. Practice with the Philip’s ‘Green TV’ project  

 

STRETCH: checklist of

environmental opportunities

Minimisation of production impact • minimisation of waste,

emissions and energy use • respect for biodiversity

Minimisation of product impact • reduction of toxic substances • minimisation of materials

consumption (i.e. through miniaturisation, weight reduction, systems integration)

• minimisation of use of non-renewable resources

• minimisation of fossil energy consumption (i.e. through energy efficiency and durable energy use)

Efficient distribution & logistics • produce where you consume • direct distribution to consumer Intensity of use • lease versus sell • collective use

Durability of products • reuse • technical upgrading • longer lifetime • repairability • refurbishing • ageing with quality

Recyclability of materials

• reduction of materials

diversity • materials cascading • design for disassembly • selected, safe disposal

STRETCH methodology showed that solutions were found in avenues which otherwise would have been eliminated beforehand.

This has resulted in a product of where the environmental load is approximately 30% lower than in the comparable current products. The advantages break down in the following way:

 

• reduction of energy

consumption: 30%

• plastic weight reduction: 32%

• reduction of hazardous

substances: 100%

• use of recycled materials:

69% of total weight • recycling potential: 93%

The cost price of this product is approximately the same as current products. The main roadblock for ‘massive introduction’ (the production of large quantities for market introduction) is the investment which has to be made to transform the present production facilities into that suitable for the ‘Green TV’. This transformation would also have consequences for suppliers, as they would have to change their parts geometries and moulds and would have to learn to work with new (mostly recycled) materials.

The above mentioned reasons suggest that the results of the ‘Green TV’ project can only be implemented ‘step by step’ over a longer period of time.

Level 3: eco-design activities, product alternatives

As is shown in the implications of level 3 eco-design activities go beyond individual companies.

 

The risks can be enormous:

 

• product alternatives might require huge investments with unsure returns

 

• product alternatives might invalidate current investments and might force a supplier base to change significantly

 

• the customer may not be prepared to buy the new products/service; if ‘environmental gains’ do not go hand in hand with other customer benefits, many people will not buy the product (however, ‘environmental gains’ are unlikely to be key purchasing criterion for the majority of people)

 

• the infrastructure to fully exploit the environmental gain is not (yet) available.

Companies wanting to start level 3 eco-design activities have therefore to approach their environmental product strategy from a much wider perspective.

The best way to do this is to link it to existing corporate and business strategy development. S&V has developed a tool to address ‘level 3’ type issues. The first two steps of STRETCH (Selection of sTRategic EnvironmenTal Challenges) therefore consist of:

 

• identification of the crucial driving forces in the business over a timescale of 3–10 years.

• making of a limited number of plausible scenarios leading to a shortlist of potential product/ market strategies.

 

This identifies potential environmental opportunities and threats in relation to the identified scenarios. These are then applied to individual products and with the help of a checklist.

 

Current LCA methodology will have to develop further to enable consideration of emissions within well defined systems boundaries, and also to include the depletion of resources

3) the opportunities are scored on different scales: • environmental scale

(i.e. eco-indicator/LCA) • customer benefit(financial,

ease of use, emotional) • business benefit(cost reduction,

expected increase in sales) • feasibility.

In order to be selected for implementation, the option must lead to a substanial decrease in environmental load. The last step is to communicate the STRETCH results to the organization and to develop the implementation plan.

At S&V brainstorm sessions have been held at a Business Unit level following the STRETCH methodology. The outcome of these sessions has indicated the substantial business and environmental potential for considerably enhancing the durability and eco-efficiency of products.

Eco-efficiency is defined here as:

Utility (units of service)

Life Cycle Impact (milliPoints)

As a result several advanced research and development (R&D) projects have been started.

The need to drastically improve the eco-efficiency of products and services through ‘level 3’ eco-design also calls for an intense stakeholder dialogue. The purpose of such a dialogue should be to test the results of the STRETCH brainstorms in a societal context. The reason for this is that to realize ‘level 3’ improvements involves big changes in companies, as a result of the risks associated with consumer acceptance and the uncertain fit into existing

physical and societal structures. In order to make ‘level 3’ improvements in a market economy all stakeholders should be prepared to adapt themselves and contribute accordingly. Prototyping of clearly communicated and agreed societal objectives and terms of reference is essential.

Rather than starting from the existing situation it is recommended to use the ‘backcasting’ technique: first define the goals to be realized in i.e. the year 2010 and go back in time in order to define what needs to be done.

The benefits of such an approach are: • focus on relevant items • clear roadmaps for the

various actors

• definition of conditions for

success both in material and

immaterial respect.

This methodology has been elaborated in a paper by the author (Stevels, 1997). The ‘backcasting’ technique has been applied to ‘take back’ of consumer electronic products. In this case the environmental validation of issues to be addressed are simple, i.e.reuse/recycling quotes and cost (Stevels, 1997).

In cases where several parts of the life cycle have to be addressed detailed environmental validation of various ‘level 3’ avenues is a major problem. Current Life Cycle Assessment (LCA) methodology will have to develop further to enable consideration of emissions within well defined systems boundaries, and also to include the depletion of resources, embedded toxicity and

reuse/recycling in (half) open product systems. In addition LCA will need to address the issue of the industrial and infrastructure transformation leading to better environmental performance of individual products.

 

Level 4: eco-design activities, sustainable product concepts

As yet, there appears to be no experience at ‘level 4’, with the lessons from ‘level 3’ changes still being learnt by leading companies.

Conclusion

In this paper the experience of a division of a Philips has been described. It is shown that eco-design can be successfully integrated into current business operations. Critical success factors for this process are indicated.

It also highlights that in order to achieve breakthroughs in reducing the environmental load of products, stakeholder dialogue must be intensified. Moreover, environmental validation methodologies such as LCA need to be extended to draw meaningful conclusions about what avenues are likely to lead to sustainability. •

References

R.A.P.M. Weterings and J.B. Opschoor. ‘Environmental space as a challenge for technological prototyping’. (RMNO publication no. 74, Rijswijk, the Netherlands, 1992)

E.U., van Weiszecker, A.B., Lovins and L.H. Lovins, ‘Factor four, twice the affluence, half the use of natural resources’ (Droemer Knaur, Mnnchen, Germany 1995)

The Brundtland Commission, ‘Our common future. Report of the World Commission on Environment and Development’, (Oxford University Press, Oxford, United Kingdom 1987)

J.C. Brezet, J.M. Cramer and A.L.N. Stevels, ‘From Waste management to Environmental Innovation’, (Rathenau Institute, The Hague, the Netherlands, 1995)

A.L.N. Stevels, ‘Design for Environment’ (UNEP, Asia Pacific Technical Monitor 1997, p. 27–33)

J.M. Cramer and A.L.N. Stevels, ‘Experiences with Strategic Environmental Product Planning within Philips Sound & Vision’ (Proceedings Of the Greening of Industry Network conference, Heidelberg, Germany, Nov. 1996)

A.L.N. Stevels, ‘A Roadmap for eco-efficient take-back of Consumer Electronics Products’ (Proceedings Globec 1996/Recycle 1996, Davos (Czechoslovakia, March 1996)

 

The Journal of Sustainable Product Design has developed a partnership with the O2 Global Network to further disseminate information and ideas on eco-design and sustainable product design. O2 Global Network is an international network of ecological designers. The O2 Global Network is organized into national O2 groups which work together to provide various services such as: O2 Broadcasts, which report live from O2 events using email and the Worldwide Web ( WWW); O2 Text meetings, a meeting place on the Web; the O2 WWW pages, which provides an overview of activities; O2 Gallery, an exhibition of eco-products on the Web; and, an O2 mailing list.

For further information on the above activities and the O2 Global Network contact: O2 Global Network Tourslaan 39 5627 KW Eindhoven The Netherlands email: This e-mail address is being protected from spambots. You need JavaScript enabled to view it tel/fax: +31 40 2428 483 internet: http:www.wmin.ac.uk/ media/O2/O2_Home.html

‘O2 News’ will update readers of the Journal on the latest eco-design issues from around the world and on O2’s national activities. In this issue O2’s activities in the Netherlands are highlighted.

Special feature: O2 Japan

 

Chair of O2 Global Network, Product designer, TNO Industrial Technology, the Netherlands

Liaison Officer, O2 Japan, Director of Open House, Japan

Product Planner, Japan

Eco-design update: news on eco-design projects worldwide

‘Take back’ at Philips

Philips have decided to set up a product ‘take back’ system in the Netherlands, thus forcing the Dutch trade organizations covering consumer electronics manufacturers and importers to become involved in the system. This means that product ‘take back’ for consumer electronics will be a reality starting January 1999. The companies will be responsible for those ‘end of life’ products which are not collected by shops and local communities. Shops will be required to accept ‘end of life’ products when selling a new one.

Mitsibushi joins the Future 500 round table

Mitsibushi has become one of the founding members of the Future 500 CEO round table. ‘Future 500’ was set up in contrast to the Fortune 500. The companies in Future 500 will be the leading companies involved in green technologies and products and will aim to significantly increase resource productivity.

Japanese Eco-Indicator

In Japan, Pré Consultancy has started to translate the Eco-Indicator ’95 system from the Dutch to the Japanese situation. The initial work has recently been completed and presented to the JLCA (Japanese Life Cycle Analysis) association. Presently, a heated debate about the type of weighting of environmental effects is going on in Japan. In contrast to the US, there has been no discussion about the necessity of such an indicator for designers.

Green consumer guidelines

SC Johnson Wax Inc. has developed a set of ‘Environmental Education Materials Guidelines for Excellence’ to be used in schools. This is based on a Roper Study in 1995, which found that customers are willing to take environmental issues into account, but do not have a basic understanding of environmental issues. SC Johnson Wax concluded that environmental education may help restore customers’ trust in industry. Furthermore, it will enable consumers to make more educated choices in purchasing

products, so that they can distinguish an ‘environmentally considered’ product from a generic product. Up to now a company could produce a green product without the consumer recognising it – unless it was highlighted. In the long term, SC Johnson Wax expects that environmental education will help generate new professionals that can deal with the complexities of combining industrial and environmental interests.