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Life Cycle Assessments of Energy From Solid Waste (PDF)

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This is also the reason for why extra transportation by passenger car to collection points is a<br />

parameter tried for both recycling and incineration to evaluate the possible effects on the<br />

results <strong>of</strong> this activity. In the scenario where this is modelled incineration without passenger<br />

car transport is also included for comparison. It is assumed that source separated waste is not<br />

collected at the house, but at collection points.<br />

The collection system starts when the waste leaves the household. The steps in the transport<br />

chain from that point will further on be described for the different treatment options<br />

respectively. The data for different vehicles used are described in section 5.8. Transport<br />

distances and type <strong>of</strong> vehicle used in the scenarios are presented in Table 3.2-4. The distances<br />

are based mainly on own assumptions. As an inspiration, transport distances for Uppsala are<br />

used in the base scenario (Sundqvist et al. 2000, appendix 2), and transport distances for a<br />

rural municipality in the middle <strong>of</strong> Sweden for the long transports scenario using information<br />

on actual treatment sites whenever possible.<br />

The different transport scenarios are:<br />

1) The base scenario with short distances<br />

2) The medium transports scenario<br />

3) The medium transports + passenger car scenario with medium distances for transports by<br />

truck and transport by passenger car from the household to the collection point in the<br />

recycling, digestion, composting and incineration options.<br />

4) The long transports scenario where the distances for the recycling options are further<br />

increased. For the other options the assumptions are generally the same as in 2).<br />

In all the transport scenarios and for all waste management options an energy use <strong>of</strong> 0.134<br />

MJ/kg waste is included for the first waste collection step. This figure is obtained from<br />

Sonesson (1997) and corresponds to the fuel consumption during a waste collection route in<br />

the city <strong>of</strong> Uppsala. Collection routes and the work connected are not the same for collection<br />

<strong>of</strong> source separated waste from collection points and for collection <strong>of</strong> mixed waste at the<br />

house. In the case <strong>of</strong> source separation and collection points the stops are fewer and the<br />

distance travelled to fill the truck may be shorter than in the case <strong>of</strong> collection at the house.<br />

The inclusion <strong>of</strong> 0.134 MJ/kg waste for all management options is consequently an<br />

overestimation for recycling and also for incineration assuming source separation.<br />

Recycling<br />

In the base scenario the waste is, in the recycling cases, assumed to be collected at a<br />

collection point close to the household, using a garbage truck. No transport by vehicle to the<br />

collection point is assumed. Thereafter the waste is transported by a garbage truck 9 km to a<br />

reloading point, plus 9 km empty return. <strong>From</strong> the reloading point to the recycling facility, the<br />

distances assumed differ between the different waste fractions and they are presented in Table<br />

3.2.<br />

In the medium transports scenario the distance from collection point to reloading point is<br />

increased to 100 km, plus 100 km empty return, and the distances therefrom to the recycling<br />

facility are also increased as can be seen in Table 3.3.<br />

The same distances as in the previous scenario are used in the third scenario, medium<br />

transports + passenger car, with the addition <strong>of</strong> 1 km extra transport by passenger to leave<br />

the waste at the collection point.<br />

33

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