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

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A general ban on recyclable and combustible waste was introduced in 1996. 933 The<br />

ban covers around 35 material streams and includes organic and household waste,<br />

paper & card, tyres, ELVs, batteries and various hazardous wastes. The purpose was<br />

to reduce the amount <strong>of</strong> waste being landfilled.<br />

The ban was introduced in the context <strong>of</strong> the dioxin emissions scandal in the late<br />

1980s. The Dutch were rebuilding their incineration capacity with much higher<br />

pollution control mechanisms, and regulatory measures were needed to ensure that<br />

incineration capacity would be used, and hence, that the high investment cost would<br />

not be wasted.<br />

The amount <strong>of</strong> waste generated in the Netherlands has been reported as ‘decoupled’<br />

from Gross Domestic Product (GDP) since 2000. 934 The amount <strong>of</strong> waste landfilled<br />

halved from 1995-2003. For incineration, the opposite trend was observed. The total<br />

amount <strong>of</strong> waste incinerated in 1995 was 4.8 Mt and in 2003 it had increased to 8.2<br />

Mt. As the incineration capacity remained constant over this period, as reported in the<br />

IVM study below, the remaining waste was exported for incineration:<br />

752<br />

29/09/09<br />

‘In 1995 and 1996 the last incineration plants were built, and from that time<br />

the government maintained a moratorium for ‘traditional’ grate incineration<br />

plants. New plants using more energy efficient technologies (such as coincineration<br />

or gasification) were allowed, but no new incineration plants<br />

became operational until 2003. So, the total number <strong>of</strong> waste incineration<br />

plants was constant at 11 in the period 1997-2003’.<br />

In certain areas incineration capacity was limited so a number <strong>of</strong> waste producers<br />

were unable to dispose <strong>of</strong> their combustible wastes thus exemptions were made so<br />

that operators could continue to landfill waste so that it was not illegally dumped. As<br />

the incineration capacity increased (to around 5.4 Mt), and the export <strong>of</strong> waste was<br />

unconstrained due to the harmonisation <strong>of</strong> waste trading via the European <strong>Waste</strong><br />

Shipment Regulation (WSR, 259/93), exemptions became harder to obtain.<br />

The main purpose <strong>of</strong> these policies was to shift waste from landfill and to ensure<br />

continued supply for the national incineration plants so that the capital expenditure<br />

outlaid in upgrading them was not wasted. This is why waste has been categorised<br />

into combustible and non-combustible fractions for the purpose <strong>of</strong> the ban and the<br />

landfill levy. This classification is meaningless in countries that are not advocating<br />

widespread EfW use, and may be counterproductive from an environmental<br />

perspective.<br />

Other points to note about The Netherlands are; that there is a general good<br />

awareness <strong>of</strong> the environment and waste related issues will be <strong>of</strong> social importance;<br />

but also that the swift implementation <strong>of</strong> the tax and ban led to under-capacity <strong>of</strong><br />

933 Eunomia et al (2007) Household <strong>Waste</strong> Prevention <strong>Policy</strong> Side Research Programme, Final Report<br />

for Defra.<br />

934 H. Bartelings, P. van Beukering, O. Kuik, V. Linderh<strong>of</strong>, F. Oosterhuis, L. Brander and A. Wagtendonk<br />

(2005) Effectiveness <strong>of</strong> Landfill Taxation, R-05/05, Report Commissioned by Ministerie von VROM,<br />

November 24, 2005.

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