C Engström Ph.D. candidate, T Hall Ph.D. candidate, A Sjöberg Ph.D.

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C Engström Ph.D. candidate, T Hall Ph.D. candidate, A Sjöberg Ph.D. A FIELD STUDY OF THE DISTRIBUTION OF DEGRADED FLOORING COMPONENTS IN A CONCRETE FLOOR C Engström Ph.D. candidate, T Hall Ph.D. candidate, A Sjöberg Ph.D.  Department of Building Technology, Chalmers University of Technology, Sweden SUMMARY: A concrete floor has been investigated for secondary emissions from degraded flooring adhesive. The results show that the distribution of emissions from degraded flooring material may vary considerably between different parts of a concrete floor. Several measurements are needed for establishing the amount of emissions in a concrete slab under a moisture-damaged flooring adhesive. BACKGROUND In Sweden, emissions from alkaline degradation of flooring adhesive on damp concrete have been suspected of causing SBS symptoms. VOCs are emitted to the indoor air but also absorbed into the underlying concrete, from where they can become a source of secondary emissions. Several thousand square meters of alkaline degraded flooring have been renovated in attempts to remedie buildings were people have complained about SBS-symptoms. Still scientific research on possible health effects from exposure to emissions from alkaline degradation of polymer flooring is scarce and it could be argued that there is a lack of standardized methods available today, to quantify these moisture damages. In an attempt to gain more experience on what parameters influence the extent (area, depth and concentrations) of an alkaline degraded flooring damage, a concrete floor was investigated for 1-buthanol and 2-ethyl-1-hexanol. Two VOC-degradation products from alkaline degradation of flooring adhesive. and were immediately put in analysis glass bottles. Samples for RH-measurements were put in test tubes. TENAX-adsorbent was used to take air samples from the glass bottles. The analysis method is further described in ....... RESULTS The results from the measurements of relative humidity are shown in figure 2. Where the PVC-flooring was still in place, the relative humidity was the same at all three depths. Where PVC- flooring had been removed the relative humidity increased with increasing depth. Where the slab was thin and the PVC-flooring had been removed (site 3), the relative humidity was the lowest. The 1-buthanol and 2-ethyl-1-hexanol measurements displayed in figure 3 and 4, show that the concentrations of both of the VOCs, were considerably higher where the PVC-flooring was still in place and the slab was thick. At site 1 along the haunch, where the concrete had been exposed to air, the amounts of 1-buthanol and 2-ethylhexanol were much lower close to the slab surface, than they were deeper down in the slab. At sites 3 and 4, where the PVC-flooring had been removed two months prior to sampling, the concentrations were very low close to the surface and higher at a of 20-30 mm. BUILDING DESCRIPTION The building is a one storey building built in 1974. The foundation of the building consists of a concrete slab with screed and thick haunches. Under the slab was a plastic diffusion barrier on shingle. This study focused on three rooms in one end of the building (fig 1), because these rooms were to have their floorings renovated. In the first room a PVC-carpet had been replaced by a wood laminate flooring a few years ago. In the second room the PVC-flooring was still in place, and in the third room the PVC flooring had been removed two months prior to the time of sampling. DISCUSSION AND CONCLUSION The results of this study show that the distribution of emissions from degraded flooring material may vary considerably between different parts of a concrete floor. One measurement is not sufficient to establish the status of a moisture-damaged flooring. It also indicates that airing out VOCs from a concrete floor will take several months. A good way to find secondary emissions is to study the moisture distribution in the concrete slab. Gaining an understanding of where to look for secondary emissions is useful for practitioners in their moisture damage investigations and for scientists trying to investigate it there is a possible connection between alkaline degraded flooring adhesive and SBS-symptoms. SAMPLING AND ANALYSIS The sampling sites are shown in figure 1. A hand held hammer drill (Hilti TE72) equipped with a large bit designed to take out cores of 90 mm in diameter was used (no watercooling). Concrete pieces from each site were removed with a hammer and chisel from the depths of 0-1, 2-3 and 4-5 cm Claes Engström, PhD-candidate Telephone: +46(0)31-772 2317 Fax: +46(0)31772 1152 engstrom@bm.chalmers.se Department of Building Materials Chalmers University of Technology SE-412 96 Göteborg, Sweden www.bm.chalmers.se