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        <div id="content-top1">Page 25 - Waste-to-Energy in the Danube Strategy Region. Challenges and Prospects</div>
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    <pre style="white-space:pre-line"><code>and benefits, PPP attracts funding from the private sector to ensure public infrastructure and

               services. Moreover, resource efficiency is improved through shorter construction time together
               with lower capital and operating costs (Rogoff and Screve 2011b, Arbulú et al. 2017).

                       Because  WtE  technologies  are  expensive  not  only  during  the  building  phase  but  also

               during the phase of operation, return on investment is also crucial. In this regard, a project’s cost

               structure should be carefully considered, both in terms of capital and operating costs. On the one

               hand, capital costs consist of expenditures for land, facility construction, technology equipment,
               engineering, installation, permitting and implementation. On the other hand, operating costs are

               influenced by labour costs, costs of chemicals and utilities, maintenance and repair expenses,

               emissions  testing  and  ash  disposal  (Rogoff and  Screve  2011b,  Arbulú  et  al.  2017).  Additional
               factors such as heat/electricity pricing and disposal also have a significant impact on ROI. This is

               especially true in the case of private ownership, for which profitability is absolutely critical.

                       A WtE plant should also run continuously because swift heating and cooling can damage

               the units and increase the operating and maintenance costs (Rogoff and Screve 2011a). To ensure
               regular operation of the facility, some states with overcapacities have to import waste from other

               countries. For example, Austria imports waste mainly from Italy and Slovenia and Germany from

               Italy, Switzerland, Ireland, Britain and others. The impending problem is that European states with

               WtE overcapacities cannot import waste from countries with insufficient incineration capacities
               (i.e.  in  Central  and  Eastern  Europe)  because  the  price  that  municipalities  pay  for  local  waste

               disposal is significantly lower than the price of incineration abroad; thus, there is no incentive (The

               Wall Street Journal 2015, Wilts and von Gries 2014). The economic challenge, in this case, arises

               when  states  are  pushed  to  import  waste  from  more  distant  places  than  from  neighbouring
               countries. Importing waste from one side of Europe to another is expensive, unecological and

               impractical.

                       WtE are capital-intensive projects requiring  supporting economic instruments for their

               faster dissemination. Such instruments include direct tools, such as subsidies, grants and loan
               guarantees,  as  well  as  indirect  measures,  such  as  high  landfill  taxes.  Implementation  of  such

               measures improves the competitiveness of WtE technologies and helps to address the economic






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