This study presents an application of an algorithm for the assessment of various policy measures and technologies on energy and environmental indicators of MSW utilization with energy recovery. Based on this algorithm, other options of the MSW management may be chosen. For example, different schemes for MBT of MSW may be chosen, resulting in different composition of HCF.
The presented estimates may serve as substantial contributions to the selection of an optimal MSW system. However, they do not strictly suggest the best system in terms of environmental pollution. The comparison of the incineration of unprocessed MSW and MBT processed MSW shows that the indicators are contrary if calculated per 1 ton of waste or per 1 kWh of produced energy. The HCF has lower volume and higher calorific value, thus producing more exhaust per 1 t of waste, but less exhaust per
1 kWh of produced energy. Emissions from the MBT process may be also be included in the overall evaluation of the system.
This study presents an application of an algorithm for the assessment of various policy measures and technologies on energy and environmental indicators of MSW utilization with energy recovery. Based on this algorithm, other options of the MSW management may be chosen. For example, different schemes for MBT of MSW may be chosen, resulting in different composition of HCF.
The presented estimates may serve as substantial contributions to the selection of an optimal MSW system. However, they do not strictly suggest the best system in terms of environmental pollution. The comparison of the incineration of unprocessed MSW and MBT processed MSW shows that the indicators are contrary if calculated per 1 ton of waste or per 1 kWh of produced energy. The HCF has lower volume and higher calorific value, thus producing more exhaust per 1 t of waste, but less exhaust per
1 kWh of produced energy. Emissions from the MBT process may be also be included in the overall evaluation of the system.
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