Anders Andrae
Ericsson Business Networks
Stockholm, Sweden
E-mail: Anders.Andrae@ebc.ericsson.se
The modelling of the system includes manufacturing (hardware and Ericsson's organisation), use stage (electricity consumption), end-of life (recycling processes) and transports. Electronic devices are modelled in depth (16 groups of components) and data from over 40 suppliers have been collected. Ericsson's organisation (development, marketing&sales, supply, installation, service and sustaining) is modelled for use of offices and business travelling.
The following main conclusions of the project are based on results for potential contributions to the environmental impact categories acidification, global warming and eutrophication, which were chosen to be the most relevant. The results predominantly reflect energy use, whereas toxicological aspects needs separate attention (could not be reliably assessed due to lack of data and reliable methods). The technology improvements shown for BC10 compared to BC8 do only describe design improvements made by Ericsson, and does not take into account potential technology production improvements made by suppliers.
Main conclusions:
The environmental impact improvements of the new model compared to the old are approximately 10%, and the uncertainty of the results is judged to be smaller than the difference between the systems.
The use stage and the manufacturing stage give the largest impacts, both for the new and the old model.
In the manufacturing stage, the hardware production is clearly dominating. Ericsson's organisation is secondly most important and hardware transport is least important.
The end-of-life stage appears to be of low or moderate importance for the energy-related impacts (1-3% decrease of the total impacts), but may be of large importance for toxicological impacts not reliably covered in this study.
Production of integrated circuits (IC) appears to be the individually most significant issue of the hardware production (approximately 20-40%). Printed circuit boards (PCB) contribute approximately 10% of the total score for hardware production.
Service (mainly travel by car) is the largest contribution for Ericsson's organisation.
The conclusions leads to the following design guidelines:
For existing MD 110 system, focus on decreasing the electricity consumption during the use stage.
When possible, reduce the total area of silicon and the total size of capsules for ICs by substitution of standard ICs with application specific integrated circuits (ASICs).
In future product development, the largest possibilities for the hardware appears to lie on a conceptual level (system design level). It appears to be difficult to reduce environmental impact significantly only by component substitution or detail construction adjustments.
In future product development it may also be considered to include organisational development as a possibility for decreased environmental impact.
Eric Williams
United Nations University/Institute of Advanced Studies
53-67 Jingumae 5-chome, Shibuya-ku
Tokyo 150-8304, Japan
Phone: 81-3-5722-2323
FAX: 81-3-5722-2324
E-mail: williams@ias.unu.edu
Dr. Manfred Zurkirch
Swisscom AG
Güterstrasse 5
CH-3050 Bern
Phone: +41 31 3423979
FAX: +41 31 3423917
E-mail: manfred.zurkirch@swisscom.com
So far, only few investigations on the ecological effects of "immaterial" services exist. Normally, they focus on one specific scenario thus often resulting in contradictory conclusions. Here, the services e-mail and ordinary mail are being compared on the basis of a modular system. That is, the infrastructure needed to provide the services is allocated to the different activities like printing, scanning, transmitting data and so on. The impact assessment of each of these elements is then treated independently. At the end, all of the boxes are connected to a modular network, therewith closing the circle again. This approach, of course, allows the user to put together any scenario and to evaluate its environmental performance. The evaluation of the different boxes (for example, printing of a document on white paper) is performed with LCA based on two impact assessment methods, namely Ecoindicator95 (NL) and the Method of Ecoscarcity (CH).
Summarizing, the eco-evaluation of the services e-mail and ordinary mail by means of a modular LCA makes a comparison of these systems very transparent and, in addition, enables the user to highlight those phases that interest him most.
Arpad Horvath
Assistant Professor
Department of Civil and Environmental Engineering
215B McLaughlin Hall
University of California at Berkeley
Berkeley, CA 94720-1712
Phone: (510) 642-7300
FAX: (510) 643-8919
E-mail: horvath@ce.berkeley.edu
A model that allows decision-makers to analyze the entire supply chain of products and processes utilized in services generation is based on economic input-output analysis approach. The author (formerly with Carnegie Mellon University) will present the use and limitations of this method (called EIO-LCA, and accessible at www.eiolca.net), and focus on a case study where this model has already been applied: the telecommunications industry. The analysis will include the material and energy inputs (nonrenewable and renewable resources), as well as the emissions and wastes (toxic discharges, hazardous waste generation, criteria pollutant emissions, greenhouse gas discharges, and ozone-depleting chemical releases) associated with the telecommunications sector.
Keith A. Weitz and Subba R. Nishtala
Research Triangle Institute
3040 Cornwallis Road
Research Triangle Park, NC 27709
E-mail: kaw@rti.org
Susan A. Thorneloe
U.S. Environmental Protection Agency
Office of Research and Development
Air Pollution Prevention and Control Division (MD-63)
Research Triangle Park, NC 27711
J. Payet and O. Jolliet
Institute of Soil and Water Management, Laboratory for Ecosystem
Management
GECOS
Swiss Federal Institute of Technology Lausanne
CH-1015 Lausanne EPFL
Switzerland, with support of ADEME (French EPA)
E-mail: jerome.payet@epfl.ch
L. Lundquist, Y. Leterrier and J.-A. E. Manson
Laboratory for technology of composites and polymers, LTC-EPFL
Swiss Federal Institute of Technology Lausanne
CH-1015 Lausanne EPFL
Switzerland, with support of ADEME (French EPA)
The example will also illustrate the sentinel approach, a new method for the assessment of life cycle impacts on ecosystems. The choice of indicator organisms is based on organisms' specific properties (resistance to chemicals, bioaccumulation) and their position within the ecosystem (position in the trophic web, fraction of biomass). This approach enables to cover a wide range of chemicals, of biodiversity; and of the diversity of ecosystems exposed to pollution.