In European legislation, waste is classified either as hazardous or non-hazardous. Hazardous waste is a waste that due to its (intrinsic) chemical or other properties poses a risk to the environment and/or human health. The legislation for waste classification was revised in 2014 in order to align it with the chemical legislation, the CLP Regulation, but some criteria and assessment procedures for the interpretation of the hazardousness were left open. Waste classification has several implications on the waste management. This report presents challenges in the hazardous waste classification. In this report, the authors express their views on the interpretation of the waste status, especially focusing on the potentially recyclable high volume waste streams. Also recommendations for the assessement of some hazardous properties are included.
This report presents the situation within the Nordic countries with respect to production and recycling of construction and demolition waste, in particular crushed concrete, in the form of aggregates, and discusses the conditions and requirements relating to environmental impacts for a possible application of the End-of-Waste option in the Waste Framework Directive. If this option is applied, the material may become a product and it will no longer be regulated by waste legislation. Regulation of crushed concrete under product legislation presents a number of challenges, particularly with respect to environmental protection. The report presents and proposes a methodology for the setting of leaching and risk-based criteria to be fulfilled by crushed concrete (and other waste aggregates) in order to obtain End-of-Waste status. It is further recommended to set impact-reducing conditions on the use of materials obtaining End-of-Waste criteria, and not to allow free use. It should be noted that the work described in this report was carried out during the period from 2010 to 2012.
This report illustrates the consequences for hazardous waste classification in the Nordic countries by introducing leaching criteria (Criterion H15). Data on secondary aggregates and waste were compared to the proposed H15 criterion and the amounts of waste exceeding the criteria were evaluated. The quality of leaching data and waste statistics varies considerably between countries and waste types. Therefore it is not possible to give a precise estimate of how much waste would have to be classified as hazardous waste if the proposed leaching criteria were introduced. However, the collected data indicated that the amount of contaminated soil, municipal waste incineration bottom ash, fly ash (both coal fly ash and bio fly ash) and metallurgical slag classified as hazardous could be expected to increase substantially if leaching criteria were introduced. The proposed H15 criteria have been developed specifically for protection of groundwater under landfill conditions, based on certain, specified assumptions and scenarios and did not address hazardousness or environmental impacts in general. The leaching test methods used are not equally suitable for all materials e.g. mining waste, and their applicability depends on a number of prerequisites including sample pre-treatment which can have a significant effect on the results. Such general use of leaching criteria and test methods developed for other purposes could lead to non-harmonised and erroneous classification.
This report presents the situation within the Nordic countries with respect to production and recycling of construction and demolition waste, in particular crushed concrete, in the form of aggregates, and discusses the conditions and requirements relating to environmental impacts for a possible application of the End-of-Waste option in the Waste Framework Directive. If this option is applied, the material may become a product and it will no longer be regulated by waste legislation. Regulation of crushed concrete under product legislation presents a number of challenges, particularly with respect to environmental protection. The report presents and proposes a methodology for the setting of leaching and risk-based criteria to be fulfilled by crushed concrete (and other waste aggregates) in order to obtain End-of-Waste status. It is further recommended to set impact-reducing conditions on the use of materials obtaining End-of-Waste criteria, and not to allow free use. It should be noted that the work described in this report was carried out during the period from 2010 to 2012.
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