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International Review of Waste Management Policy - Department of ...

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verbrandbaar bouw- en sloopafval” (Regulation on non-recyclable and noncombustible<br />

C&D waste) prescribes that recyclable and combustible C&D waste<br />

cannot be landfilled. C&D waste is defined as non-recyclable and non-combustible if<br />

the >60 mm fraction contains more than 85% <strong>of</strong> the following materials:<br />

891<br />

• Contaminated stony material<br />

• EPS insulated concrete<br />

• Thermal/acoustic insulation material based on minerals<br />

• Tar and bitumen ro<strong>of</strong> material<br />

• S<strong>of</strong>t stony material<br />

• Preserved wood based on “Wolman salts” (Cu, Cr, As)<br />

• Glass<br />

• Non-separable combinations made <strong>of</strong> at least 50% <strong>of</strong> the above materials<br />

For demolition the “Asbestbesluit” (Asbestos Regulations) require the separate<br />

removal and collection <strong>of</strong> asbestos. The “Regeling scheiden en gescheiden houden”<br />

(<strong>Waste</strong> Separation and Storage Regulations) require the separation at source <strong>of</strong><br />

hazardous waste.<br />

In the Netherlands, recyclable/reusable wastes from construction and demolition<br />

have been banned from landfill since 1997. These wastes include masonry &<br />

concrete rubble, metals, untreated wood, paper and cardboard etc. Currently, about<br />

95% <strong>of</strong> all C&D waste is recovered.<br />

In Germany unsorted construction and demolition wastes have been banned from<br />

landfill sites since 2001. The Closed Substance Cycle and <strong>Waste</strong> <strong>Management</strong> Act<br />

was an overarching legislative development in waste management in Germany,<br />

coming into force in September 1996. Its aim was to make producers and<br />

consumers radically rethink approaches to waste: “integrating product responsibility<br />

through economic decision-making process, with the aim <strong>of</strong> building a life cycle<br />

economy that avoids waste generation”. Developing from this, and in response to<br />

pressures to improve recycling and recovery performance, a number <strong>of</strong> other<br />

regulations have come into force, two <strong>of</strong> which are focused on here:<br />

• Commercial <strong>Waste</strong>s Ordinance 2002<br />

• <strong>Waste</strong> Wood Ordinance 2002<br />

Commercial <strong>Waste</strong>s Ordinance 2002<br />

The German Regulations, the “Commercial <strong>Waste</strong>s Ordinance, 2002” came into force<br />

on 1 st January 2003, and provide a minimum separation requirement for pretreatment<br />

facilities receiving both municipal and commercial wastes, including<br />

specific construction and demolition wastes. To facilitate high levels <strong>of</strong> recovery,<br />

Section 8, Paragraph 1 <strong>of</strong> the Ordinance specifies a number <strong>of</strong> wastes which should<br />

be held, stored, collected and hauled for recovery, separately. These wastes are: (i)<br />

glass, (ii) plastic, (iii) metals, (v) concrete, bricks, ceramics (or a mixture <strong>of</strong> these).<br />

The Ordinance provides a derogation from this separation, on the basis that these<br />

waste streams can only be mixed with those set in the Annex to the Ordinance, and<br />

that the initial quantity and purity <strong>of</strong> the these five categories <strong>of</strong> input waste streams<br />

are produced as separated streams for substance, or energy recovery (unless it can<br />

be demonstrated that there is a technical reason why this is not possible).<br />

<strong>International</strong> <strong>Review</strong> <strong>of</strong> <strong>Waste</strong> <strong>Policy</strong>: Annexes

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