C-06 Transport of wastes to landfill, incineration and recycling facilities – complete LCA

Aspect C-06 Transport of wastes to landfill, incineration and recycling facilities – complete LCA
Description
The transportation distances are likely to be different, depending on the EoL scenarios. For example, whereas a landfill facility is likely to be found in every city, a recycling plant may be far away as, for example, only one exists in a country exists.In this context, how should representative distances according to different waste EoL routes be defined for complete LCA?

related study objective

stand-alone LCA comparative assertion

related study phase

goal and scope definition inventory analysis (LCI) impact assessment (LCIA) interpretation reporting

relevant for

new buildings existing buildings construction products screening LCA simplified LCA complete LCA
Provisions The transport of wastes or recycled products to EoL facilities should be included for complete LCA, even if maybe of assumed minor relevance.This aspect is likely to be predefined, for example in generic LCA data for EoL processes or in each national EPD programme, and may be adopted within a given LCA study.
Rules from:

EN 15804

 

6.3.4.6 End-of-life stage
6.3.8 Developing product scenarios
7.3 Scenarios and additional technical information
7.3.4 End of life


Guidance
For recycling and disposal routes, the distances will vary, depending on each national context [SBA 2012]. Transport distances for different waste types may also vary according to the number of treatment sites. For example, hazardous waste may have the longest transport distance, owing to the limited number of sites, whereas inert waste may have the shortest (http://www.sepa.org.uk/waste/waste_infrastructure_maps.aspx or http://www.landfill-site.com/html/how_many_landfills.php). National waste management plans or waste infrastructure maps may help in identifying the locations of waste management sites.Data may be currently available for transport of waste between the demolition site and sorting plant: e.g. for the French context see the report from [ADEME 2003]. For example, current practice in generic databases or EPD programmes may take into account:- between 10 and 30 km for inert and non-hazardous wastes, as well as for incineration with energy recovery;- around 100 km for hazardous wastes.For recycled products sent to a recycling facility it is likely that the distance will be higher because, to date, the number of recycling facilities is still low, leading to higher distances than for landfill facilities. As an average value, 250 km for trucks can be assumed. This figure may be revised if more accurate data are available in a national context, and if the EoL transport is found to be significant in the final results.

 


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