Proceedings of the 1997 IEEE International Symposium on Electronics and the Environment. ISEE-1997 1997
DOI: 10.1109/isee.1997.605314
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Environmental assessments of electronics: a new model to bridge the gap between full life cycle evaluations and product design

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Cited by 21 publications
(8 citation statements)
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“…Within the three hazard groups there is a relative prioritization of hazard metrics similar to GS, where certain metrics yield higher TPI values. The three hazard group scores are weighted equally, combined, and scaled into a 0-100 value (0 = no hazard, 100 = very hazardous) [18,19]. For example, ethylene has very high HH impacts but minimal W-E and OH impacts, with resultant TPI = 35.…”
Section: Industrial Methods: (2)mentioning
confidence: 99%
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“…Within the three hazard groups there is a relative prioritization of hazard metrics similar to GS, where certain metrics yield higher TPI values. The three hazard group scores are weighted equally, combined, and scaled into a 0-100 value (0 = no hazard, 100 = very hazardous) [18,19]. For example, ethylene has very high HH impacts but minimal W-E and OH impacts, with resultant TPI = 35.…”
Section: Industrial Methods: (2)mentioning
confidence: 99%
“…The TPI offers a higher resolution scoring method, which can serve a different purpose than hazard screening. For example, one alternative postprocessing method is to sum chemical scores of mixtures into a single value [19]. For this case study, however, it was desirable to have the robustness of two sets of assessment scores as the basis for the hazard screening, therefore it was necessary to post-process the TPI results in such a way that comparisons to the GS results could indeed be made.…”
Section: Sources Of Uncertainty and Errormentioning
confidence: 99%
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“…Here, we summarize the computational structure and input parameters. The basic EUTPI requires 3 input parameters to capture human health impacts, environmental impacts, and other safety considerations for substances (Nissen et al 1997). These parameters are denoted by occupational exposure limits (MAKs) or EU carcinogenicity classifications, German water hazard classifications (WGK), and Risk phrases (R‐phrases), respectively.…”
Section: Methods and Datamentioning
confidence: 99%
“…Hazard‐based toxicity assessment tools are essential to facilitate alternative assessments in the quest to use safer, nontoxic materials for designing and manufacturing consumer products. The development of the Toxic Potential Indicator (TPI) model at the Fraunhofer Institute in Germany was motivated by the need for an environmental assessment method that is more transparent than comprehensive life cycle analysis (LCA) to rate hazardous materials used in commercial products and industrial processes (Nissen et al 1997, 1998; Yen and Chen 2009). The reasoning is that although traditional LCA can provide quantitative comparisons of environmental impacts across various stages of materials' life cycles (ISO 14040 2006), it is difficult to apply in market settings with fast product turnover rates (e.g., electronics) because it is tedious and requires special expertise not necessarily accessible to manufacturers (Millet et al 2007).…”
Section: Introductionmentioning
confidence: 99%