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Miljø- og samfundsøkonomisk vurdering af ... - Miljøstyrelsen

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Important pre-conditions for the assessments made in this project can be found in chapter 2 of the<br />

report. In Tabel 2 can be found the typical composition of household waste from single family and<br />

multey storey households. Tabel 3 informs about separation effeciency in the houdehold for each<br />

recyclable fraction. Tabel 4 and Tabel 5 include information on type and size bins applied in the<br />

different scenarios as well as the emptying frequency. Tabel 11 shows the sorting effeciency at<br />

centralised sorting planst for each type of recyclabe fraction being fine sorted.<br />

Assessment of the recycling rate<br />

The recycling rate can be meassured in two ways. One way is to determine recycling by the total<br />

amount of the different waste fractions collected for recycling as a percentage of the total<br />

amount of household waste (including materials for recycling, see footnote 1), i.e. no subsequent<br />

separation of materials is taken into account. In principle, this corresponds to the method<br />

presently applied for measuring compliance with official targets. Alternatively, the recycling rate is<br />

calculated as the amount of materials actually recycled and sold to the recycling industry,<br />

i.e. the collected amount of the waste fractions for recycling is deducted the amount discarded later<br />

due to technical or quality reasons. The assessment of environmental impacts and economics is<br />

based on the actual amount recycled.<br />

The recycling rates in the different scenarios are shown in Figure A. The rate depends largely on the<br />

assumptions made for efficiency at household level with respect to separating the different waste<br />

fractions. Ambitious but realistic seperating efficiency is applied as achieved in full scale operations<br />

in Danish (and Swedish or German) recycling schemes. In all scenarios recycling rates are<br />

significantly increased compared to the baseline scenario. In scenarios 4 and 7, having no source<br />

separation of organic waste, the recycling rate has increased less than in the other scenarios where<br />

organic waste is separated at source, anaerobicly digested and spread on farmland.<br />

Source separated organic waste is either treated at an Aikan anaerobic digestion (AD) plant (2A,<br />

3A, 5A and 6A) or a manure-based anaerobic digestion facility (2F, 3F, 5F and 6F). The amount of<br />

organic waste "collected for recycling" is the same for the two technol<strong>og</strong>ies; however, the actual<br />

recycling rate is less for the manure-based facility that requires a more effective pre-treatment,<br />

resulting in a larger loss of organic material. Source separation of organic waste increases recycling<br />

up to 22 % points (can be seen by comparing scenarios 3 and 4).<br />

In the scenarios 2A, 2F and 2Z, the recycling rate is increased due to source separation of the<br />

organic household waste and more effective source separation of paper compared to the baseline<br />

scenario. Scenarios 3A, 3F, 3Z and 4 also involve source separation of cardboard, plastic and metal,<br />

which - as compared to scenario 2 - increases the fraction "collected for recycling" by 6% points and<br />

the fraction "actually recycled" by 3% points.<br />

Miljø- <strong>og</strong> samfundsøkonomisk <strong>vurdering</strong> <strong>af</strong> muligheder for øget genanvendelse <strong>af</strong> papir, pap, plast, metal <strong>og</strong> organisk <strong>af</strong>fald fra<br />

dagrenovation<br />

23

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