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Characterisation factors for life cycle impact assessment of sound emissions 1
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Cucurachi S.
a*
, Heijungs R .
a
3
a
Institute of Environmental Sciences (CML), Leiden University, P.O. Box 9518, 2300 RA Leiden, 4
The Netherlands 5
*
Corresponding author. Tel.: +31 (0) 71 527 1478; e-mail: cucurachi@cml.leidenuniv.nl 6
This is an earlier version of the following article:, which has been published in final form at 7
19 http://onlinelibrary.wiley.com/doi/10.1002/ieam.269/abstract. 8
This document is the unedited Pre-print Version of a Submitted Work that was subsequently 9
accepted for publication in Science of the Total Environment, copyright © ELSEVIER after 10
peer review. To access the final edited and published work see: 11
http://www.sciencedirect.com/science/article/pii/S0048969713008619 12
(DOI: 10.1016/j.scitotenv.2013.07.080) 13
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Abstract 15
Noise is a serious stressor affecting the health of millions of citizens. It has been suggested that 16
disturbance by noise is responsible for a substantial part of the damage to human health. However, no 17
recommended approach to address noise impacts was proposed by the handbook for life cycle 18
assessment (LCA) of the European Commission, nor are characterisation factors (CFs) and appropriate 19
inventory data available in commonly used databases. This contribution provides CFs to allow for the 20
quantification of noise impacts on human health in the LCA framework. Noise propagation standards 21
and international reports on acoustics and noise impacts were used to define the model parameters. 22
Spatial data was used to calculate spatially-defined CFs in the form of 10-by-10-km maps. The results 23
of this analysis were combined with data from the literature to select input data for representative 24
archetypal situations of emission (e.g. urban day with a frequency of 63 hertz, rural night at 8000 25
hertz, etc.). A total of 32 spatial and 216 archetypal CFs were produced to evaluate noise impacts at a 26
European level (i.e. EU27). The possibility of a user-defined characterisation factor was added to 27
support the possibility of portraying the situation of full availability of information, as well as a 28
highly-localised impact analysis. A Monte Carlo-based quantitative global sensitivity analysis method 29
was applied to evaluate the importance of the input factors in determining the variance of the output. 30
The factors produced are ready to be implemented in the available LCA databases and software. The 31
spatial approach and archetypal approach may be combined and selected according to the amount of 32
information available and the life cycle under study. The framework proposed and used for 33
calculations is flexible enough to be expanded to account for impacts on other target subjects than 34
humans and to other continents than Europe. 35