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    <pre style="white-space:pre-line"><code>The calculation may also be considered conservative due to the assumptions regarding

               the circular economy targets themselves. Firstly, looking at MSW management throughout the EU
               28  +  Iceland,  Norway  and  Switzerland,  it  is  apparent  that  those  countries  who  have  already

               achieved the landfilling target in fact have even lower levels of landfilling. Switzerland has 0%,

               while five countries, including Germany, have a landfill rate of 1%. Austria and Finland each landfill

               3% of MSW, while Norway has a rate of 4% (Eurostat 2018a). This circumstance would suggest

               that where effective landfilling legislation is in place levels even lower than 10% are achieved and
               thus the potential for WtE could be more than 25%. Similarly, the recycling target is measured as

               the  percentage  of  MSW  that  is  separately  collected  for  recycling  purposes.  However,  not  all

               separately collected waste is ultimately recyclable. A conservative estimate by CEWEP and the
               European Commission states that 8% of separately collected waste is ultimately sent to recovery

               operations and 2% to landfill (Stengler 2016). Thus, once again, the proportion of MSW available

               for energy recovery would increase beyond 25%. Indeed, the net effect could be significant. In the

               case  of  Romania,  for  example,  the  estimated  gap  in  Table  2  is  negative,  suggesting  an
               overcapacity. However, given its relatively high level of MSW generation, these additional inputs

               would likely result in a positive gap, indicating additional required capacity.

                       Finally, it is worth once again pointing out that the choice of Eurostat data was made in

               order to maintain a certain level of comparability and reliability. Nevertheless, as discussed above,
               the definition and method of measurement for some figures may vary across countries. To that

               end the EU-level initiatives in this area also strongly aim at achieving homogenization with regard

               to definitions and measurements.  The Czech Republic offers a clear example of the necessity of

               such efforts. Eurostat relies on MSW data from the Czech Statistical Office despite the fact that
               the competent authority in the country is the Ministry of Environment (Czech Statistical Office

               2016). The former provides an estimated figure of 3.58 million tonnes of MSW in 2016, while the

               latter cites a figure of 5.612 million tonnes based on its collected data (Ministry of the Environment

               of the Czech Republic 2018). Long-standing discussions between the two authorities are likely to
               resolve this discrepancy, but in the meantime it is worth considering both sets of data (Czech

               Statistical Office 2016). Using the MZP figure, a capacity gap of 677,000 tonnes is calculated, which

               may be regarded as a more realistic estimate in the case of Czech Republic. Once again, this



               Project co-funded by the European Union
                                                                                                           34</code></pre>
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