Abstract
Separate collection of valuables from waste is of growing importance for the conservation of resources and the mitigation of greenhouse gas emissions from landfills. Moreover, the separation of certain waste fractions, such as food waste, is necessary to ensure that landfills and – more importantly – incinerators are managed properly. It is therefore necessary to examine the reasons and motivations for separating waste. Separation and recycling of waste fractions should decrease the overall cost of waste disposal for citizens and public bodies. This can only happen if the authorities take into consideration some important “stumbling blocks,” i.e. physical and socioeconomic indicators and prerequisites, when introducing a recycling system. Four examples (landfill tax as an incentive for separate collection, recycling of used paper and cardboard, collection of bio-waste, recycling of mixed packaging waste) have been investigated in order to evaluate the reasons for successful and unsuccessful attempts at resource recovery. Economic incentives for waste segregation are very important and should be tested in pilot studies or through simulation games, because major differences between opportunity costs and costs for alternative treatment options may lead to unwanted behavior by waste producers and/or citizens. Furthermore, citizens’ behavior regarding the separation of valuables, their cultural background with respect to waste management, and social norms must be taken into account when planning collection schemes. Obviously, convenient access to collection systems is essential. Citizens must become accustomed to these systems; long-term awareness raising helps to optimize the successful collection of recyclables.
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Notes
- 1.
The dissipation dilemma can be demonstrated using platinum (Pt) as an example: Pt is used in the chemical industry (catalysts, laboratory equipment) and for the production of glass (fiber glass nozzles). The recycling rates are >80% and >95%, respectively. As to Pt from automobile catalysts, the recycling rate is <<50% [16], though the loss of Pt from car catalysts during the use phase has been minimized. The recovery of Pt from smaller devices used by consumers is far less.
- 2.
The economic restraints for deposits in the case of products with a long usage period cannot be described here in detail. It should be noted that the value of a complex product after operational life cannot be estimated reliably. Moreover, high deposits for products which are in use for a long time extract considerable liquidity from the capital markets.
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Friege, H. (2017). Separate Collection of Waste Fractions: Economic Opportunities and Problems. In: Maletz, R., Dornack, C., Ziyang, L. (eds) Source Separation and Recycling. The Handbook of Environmental Chemistry, vol 63. Springer, Cham. https://doi.org/10.1007/698_2017_24
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