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Waste reduction final report -4 - Test Input

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Environmental protection in Switzerland is based on the Federal Constitution of the Swiss<br />

Confederation (Bundesverfassung BV, 1999 27 ). In Articles 73 and 74, the Constitution<br />

requires a sustainable handling of the environment (principle of sustainability). Harmful<br />

effects shall be avoided (precautionary principle) and where this is not possible, the causer is<br />

responsible for resulting costs (costs-by-cause principle or polluter pays principle). Based on<br />

these articles the government has issued numerous laws, regulations and guidelines [BV<br />

1999].<br />

Laws<br />

The Swiss parliament issued the Law for Environmental Protection in 1983<br />

(Umweltschutzgesetz USG). The law contains the basic principles of waste management,<br />

without treating construction waste specifically. Article 30 requires that waste should be<br />

avoided or reused as far as possible. As to articles 30a to 30d, the government is allowed to<br />

prohibit or confine waste-causing products, to require suitable recycling from producers or to<br />

prescribe the reuse of waste if this is ecologically and economically reasonable [USG 1983].<br />

For example, there has been discussed the idea of constraining exploitation of gravel in order<br />

to foster the use of secondary construction materials. However, this is not a primary interest<br />

of the gravel sector and additionally, the Federal Constitution guarantees commercial<br />

freedom of action. This example shows that there would be a certain potential to change<br />

something by the politics, but that it is very hard to reconcile the different statements.<br />

Regulations<br />

Numerous regulations relate to the Law for Environmental Protection. The<br />

major regulation in the field of waste management is the Technical Ordinance on <strong>Waste</strong><br />

(Technische Verordnung über Abfälle TVA, 1990). Article 9 deals with construction waste; it<br />

requires the separation of the latter on building sites into the following categories:<br />

a. Unpolluted excavated material and soil<br />

b. <strong>Waste</strong> which can be deposited on a landfill for inert materials without further<br />

treatment<br />

c. Burnable waste as wood, paper, cardboard or plastics<br />

d. Other waste<br />

Excavated material and soil should be as far as possible used for remediation projects<br />

(article 16) provided that it is pollution free according to article 3 paragraph 7. Burnable<br />

waste should be burned in appropriate waste incineration plants if it is not possible to exploit<br />

it further (articles 11 and 16). Authorities can require waste owners to recycle their waste if<br />

this is ecologically reasonable, technically feasible and economically bearable (Article 12).<br />

Article 15 obliges the cantons to write a waste plan describing the canton’s waste<br />

management system and to issue statistics on yearly waste quantities [TVA 1990]. This task<br />

is done well in the field of municipal waste, but there are big gaps in the management of<br />

construction waste. Mainly, this is due to two reasons: Firstly, construction waste is handled<br />

mainly by privatised companies and there are no obligations for declaration of waste on<br />

construction sites or for plants receiving those materials. Secondly, waste flows between<br />

cantons as well as waste types are multiple and difficult to observe. These facts make it<br />

difficult for the authorities to observe the path of construction waste.<br />

The TVA is subject to a revision. Technique has evolved much, shortage of disposal sites is a<br />

problem and the amount of construction waste will rise. Concerning construction<br />

27 Originally, it was established in 1848; a thoroughly revised version became effective in 1999.<br />

89

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