2003
DOI: 10.1016/s0045-6535(03)00053-5
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Ranking the risks of 12 major environmental pollutants that occur in Japan

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Cited by 40 publications
(27 citation statements)
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“…[5] As common indices, lifespan reduction due to adverse health effects, or similar reduction but with adjustment for quality of life, are both widely used. For example, Gamo et al [6] used an index called lost life expectancy (lifespan reduction) to evaluate replacement of a termite control agent; and Gamo et al [7] used this same index to rank major environmental pollutants. Kishimoto [5] used an index based on loss of quality-adjusted life-years (QALYs: lifespan adjusted for quality of life) in the detailed risk evaluation of toluene; and Cohen et al [8] used this index to compare the benefit of polysaturated fatty acid, with the risk of methyl mercury, in fish consumption.…”
Section: Methods Using a Common Risk Indexmentioning
confidence: 99%
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“…[5] As common indices, lifespan reduction due to adverse health effects, or similar reduction but with adjustment for quality of life, are both widely used. For example, Gamo et al [6] used an index called lost life expectancy (lifespan reduction) to evaluate replacement of a termite control agent; and Gamo et al [7] used this same index to rank major environmental pollutants. Kishimoto [5] used an index based on loss of quality-adjusted life-years (QALYs: lifespan adjusted for quality of life) in the detailed risk evaluation of toluene; and Cohen et al [8] used this index to compare the benefit of polysaturated fatty acid, with the risk of methyl mercury, in fish consumption.…”
Section: Methods Using a Common Risk Indexmentioning
confidence: 99%
“…Kishimoto [5] used an index based on loss of quality-adjusted life-years (QALYs: lifespan adjusted for quality of life) in the detailed risk evaluation of toluene; and Cohen et al [8] used this index to compare the benefit of polysaturated fatty acid, with the risk of methyl mercury, in fish consumption. Disability-adjusted life expectancy years (lifespan with adjustment for disabilities caused by disease) is used as an index in calculations of the worldwide burden of disease by the World Health Organization (WHO); [9] and Havelaar et al [10] used this index to compare the risk of bromate [6] [7] Estimate using structural equation modeling [14] Common The problem with this approach is that its estimations require the results of human epidemiological studies, and many potential replacement substances do not even have sufficient animal test data, let alone human epidemiological study results. In sum, this approach is less executable than the general risk analysis method described in Subchapter 2.1.…”
Section: Methods Using a Common Risk Indexmentioning
confidence: 99%
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“…Several methods are available for assessing toxicity varying from classifications based on physico-chemical properties (as is relevant for nanomaterials), animal experiments and/or modelling frameworks (such as QSAR to predict toxicity effects with/without including a correlation with physicochemical properties), or PBPK-models to determine the exposure-dose-response relationship (Hristozov et al, 2012). Then, scores need to be aggregated, which is mainly done by multiplying exposure and effect (see for example (Gamo et al, 2003;Juraske et al, 2007;van Asselt et al, 2013), although one study added the scores (Penrose et al, 1994).…”
mentioning
confidence: 99%