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Life Cycle Assessments of Energy From Solid Waste (PDF)

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In this study, electricity generated from hard coal is chosen as the marginal technology. The<br />

data for electricity produced from hard coal is from Frees and Weidema (1998), these data are<br />

further described in section 5.7. As discussed above other alternatives may also be considered<br />

and this should preferably be done in a continuation <strong>of</strong> this study.<br />

3.3 Heat production<br />

3.3.1 Heat source<br />

In this study heat produced when handling waste by incineration, anaerobic digestion or<br />

landfilling is credited the waste treatment option by subtracting heat produced from another<br />

source (avoided product systems are explained in chapter 2). Heat produced through the waste<br />

management is assumed to be transferred to the district heating system. The 1998 composition<br />

<strong>of</strong> energy carriers contributing to the 44.1 TWh heat delivered by the district heating facilities<br />

in Sweden are shown in Table 3.1. As can be seen the major contribution is from forest fuels,<br />

this amount has increased by four times since 1990. The main forest fuels are forest felling<br />

residues and by-products from the forest industries (Energimyndigheten 1999).<br />

Table 3.1 <strong>Energy</strong> supplied from different sources to the district heating system in Sweden during 1998<br />

(Energimyndigheten 1999).<br />

Fuel<br />

<strong>Energy</strong> supply (TWh)<br />

Forest fuels 14.7<br />

Heat pumps 7.4<br />

Oil 5.5<br />

<strong>Waste</strong> 5.0<br />

Surplus heat etc 3.6<br />

Coal 3.4<br />

Natural gas and liquefied petroleum gas 3.3<br />

Peat 3.1<br />

Other bi<strong>of</strong>uels 2.9<br />

Electric boilers 1.8<br />

In this study, the ideal data would be the long-term base load marginal as discussed in 2.1.2<br />

and 2.3.2. Which source this is may be discussed. One key assumption is whether the market<br />

for district heating has an up- or down-going trend. If there is an increasing use, the most<br />

preferred alternative would be on the marginal and if the use is decreasing the least preferred<br />

alternative would instead be defined as the marginal technology. Increasing the districtheating<br />

share <strong>of</strong> the total heating may be considered to be in line with aiming towards<br />

sustainable energy use. Transforming systems where electricity is used for heating buildings<br />

to being supplied with district heating is one example.<br />

Assuming an upward trend, the discussion may be that bi<strong>of</strong>uels are preferred from a<br />

greenhouse effect perspective and that the availability in Sweden is comparably high. On the<br />

other hand, on the global market, biomass will become increasingly scarce and also in<br />

Sweden different uses for biomass compete for the available resources.<br />

Incineration <strong>of</strong> waste is another possible marginal heat producing technology if other options<br />

<strong>of</strong> handling this waste is not considered to be significantly more preferable and the amount <strong>of</strong><br />

combustible waste is sufficient. The waste may be household waste or waste from other<br />

sectors, e.g. the building sector. It has been noted that other types <strong>of</strong> waste is the competing<br />

heat source in Sweden today (ÅF-IPK 1998). This is because the current waste incineration<br />

capacity in Sweden is limited. If a choice leads to increased or decreased incineration <strong>of</strong> a<br />

specific waste fraction, this is likely to decrease or increase the incineration <strong>of</strong> other waste<br />

fractions and an increase or decrease <strong>of</strong> landfilling <strong>of</strong> this fraction resulting in a constant use<br />

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