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Waste reduction final report -4 - Test Input

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It is recognized that lean concrete will be the place for recycled mixed aggregates. It can be<br />

introduced at many places on the construction site without problems. Examples for this (and<br />

for other types of recycling concrete, too) are given in two brochures by the canton of Geneva<br />

[GE 2009]. In order to transfer the current knowledge to the regarding persons and to<br />

overcome prejudices, the project “gravel for generations” has been started.<br />

Another discussion point concerns possible pollutants in mixed mineral material and their<br />

behaviour. In Switzerland, a study was accomplished about pollutants in secondary<br />

construction material in general [VSS 2002].<br />

Secondary construction materials do not contain many pollutants; additionally, most of them<br />

are inorganic. Indeed, concentrations of chemicals are higher in recycled mixed aggregates<br />

than in other secondary materials. The authors claim that high quality requirements for all<br />

secondary materials would ensure security for human beings and the environment. This way,<br />

accumulation of pollutants such as nitrogen compounds or chromium in ground water is<br />

avoided.<br />

Asphalt<br />

About 50% of asphalt waste is used directly on site, e.g. by a procedure using heat; the other<br />

50% are recycled into recycled asphalt aggregates or landfilled. However, there are hold<br />

some discussions about the recycling of asphalt: A total of about 6 MT pavements contains<br />

tar, which corresponds to about 5% of the total embedded asphalt [ARV 2008]. Abrasion<br />

of material comprising PAH can trigger health problems.<br />

Today, materials with more than 20,000 mg PAH per kg binding agent are allowed only to be<br />

used with restrictions and current policy works suggests to sort out and eliminate the tarcontaining<br />

fraction [FOEN 2008c]. In contrast to this, the industry claims that there exist<br />

methods for a safe reuse of these materials [Killer 2008]. Even so, the next revision of the<br />

ChemRRV will probably implicate a prohibition of new bitumen containing road surfaces<br />

and PAK parts in the upper layers of roads [Stadt Zürich 2007]. The binding material shall be<br />

taken out of the cycle by incineration.<br />

Excavation material<br />

Excavation material is generated in high amounts, contaminated (only 5-10%) or pollutionfree.<br />

As there is no obligation to capture the amount, only estimations can serve as lead.<br />

Today, estimations give figures around 40 to 60 Mm 3 per year, and given that big projects<br />

and high construction activity are expected, this figure will rise in the next years. Today, the<br />

material is mainly used for backfilling or reclamation of gravel pits or construction sites. The<br />

remaining parts are used in another form or are landfilled.<br />

Depending on the canton’s space availabilities, scarcity of landfill space will become an<br />

urgent problem. Today already, materials are transported over big distances with lorries. The<br />

current TVA revision will deal with this problem. Materials with good construction<br />

properties can be used as construction materials, but for the remaining parts, solutions for insitu<br />

or other use of excavation have to be established. A study accomplished by the<br />

Hochschule für Technik, Rapperswil was ordered by the FOEN [FOEN 2008b]. The study<br />

compiled examples of sustainable in-situ use of excavation materials in landscape forming.<br />

Identified problems concerned the quality of the remaining excavation material, space<br />

constraints and interim storage. Furthermore, it concluded that it was easier to reuse<br />

excavation material at big construction sites than at smaller ones. From the economic side of<br />

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