First results of a pilot decontamination in a
PCP polluted building by means of a humidity controlled thermal process
Abridged translation. The original paper was written in
German and contains additional information.
W. von Rotberg1, M. Gagelmann2, H. Piening3,
R.W. Sieke4, S. Michaelis5, N. Wilke1 and
K.Roux6
1Thermo Lignum GmbH, Landhausstrasse 17, 69115
Heidelberg, Germany;
2Öko-Consult Dr.rer.nat.habil. M Gagelmann GmbH, Wormserstrasse 9,
69198 Schriesheim, Germany;
3Bayrische Verwaltung der Schlösser und Gärten, Residenzstrasse 1,
80333 München, Germany;
4Technologie Consulting GmbH, Echterngrund 19, 30657 Hanover;
5Thermo Lignum Buehner & Co. GmbH, Paul-Lincke-Ufer 42-43, 10999
Berlin;
6Thermo Lignum UK Limited, 19 Grand Union Centre, London W10 5AS, UK
Introduction
Up till the early Eighties preventative treatments of construction and
ancillary materials even in interiors and of wooden and textile objects as well
as those made of, e.g., paper and leather as a precaution against insect and
fungal attack used to be carried out using pentachlorphenol (PCP) as active
ingredient. PCP evaporation from such large material surfaces treated in such a
manner can reach levels of concentration even today which are still hazardous to
human health (Gagelmann and Fonfara, 1992).
It is possible to record even today very high levels of interior
contamination from pentachlorphenol (PCP) particularly in buildings of
historical significance with many wooden interior fittings. There are as yet no
appropriate methods to decontaminate protected historic buildings or objects.
All processes in use hitherto, such as the steam-tight panelling, the removal or
encasement and surface coating of contaminated construction elements cannot be
justified from a curatorial point of view. It was therefore the aim of the
investigation to test the application of a new humidity-controlled thermal
process with which it is possible to evaporate out the volatile wood preserver
ingredients contained in the surfaces to be treated so as to arrive at a
distinct improvement of interior air quality.
The humidity-controlled thermal treatment processed developed and patented by
Thermo Lignum has been successfully used for several years for the purpose of
disinfestation from insect pests in items made of organic materials, notably
works of art, museum exhibits, antiques, libraries and archives. Another
application is the treatment of mould on objects and dry rot in buildings.
In an earlier pilot project it was possible to demonstrate the beneficial
effect of the Thermo Lignum method when an small reconstructed cottage was
treated against wood-boring infestation in its structural timbers. The building
was heated to a core temperature of 55 °C in the same way as described above.
This particular infestation treatment was completed in under 24 hours due to its
size and the fact that a holding phase of one to two hours is sufficient to
achieve a 100% kill rate of all forms of infestation. This was the first time
this pioneering treatment involving combined heating and humidity control had
been carried out on a whole building (Zeuner, 1997).
Materials and Methods
After preliminary tests on a laboratory scale the applicability in principle
of a humidity-controlled thermal process for the detoxification of contaminated
interiors could be confirmed. The process consists of the heating of a closed
room whilst simultaneously controlling its humidification. The room to be
treated is sealed off tightly and is slowly heated to 60°C by inducing hot air
from a closed-circuit heating system developed and patented by Thermo Lignum
GmbH,Germany, which ensures an even air distribution throughout the room. (The
maximum heating capacity/hour of the modular system is 8,000 m3 thus
making large-scale decontamination possible). Structural damage due to drying
out is pre-empted by keeping the relative humidity (50%) in the induction air
constant by means of a computer-assisted control unit. Room temperature
increases gradually guided by the wood and masonry core temperatures (Nicholson
and von Rotberg, 1996). After reaching the target temperature there
follows a holding phase lasting several days up to several weeks during which
time the contaminants are mobilised.
At the same time the mobilised contaminants are broken down by means of
oxidation in the sealed reaction compartment of a separate parallel air cycle.
The reactive oxidation product is generated for this purpose in an ozone
generator in which oxygen molecules are converted into radicals which form ozone
structures in high levels of concentration with half lives between 70 msec and
70 sec.
To verify the success of the decontamination treatment air measurements were
taken after a 14 to 16 hour long closing of the room and at temperature levels
typical for residential occupation. Air sampling (2-3 m3; 2 m3/hour)
was done on fibre glass filters (dust phase) and polyurethane foams (gaseous
phase) (Leitfaden 1994; VDI 4300, 1994). Following specific
extraction with toluene analysis gas chromatography mass spectrometry was
carried out.
Results and Discussion
In the first phase of the pilot decontamination a severely PCP contaminated
room of an approximate volume of 72.5 m3 (room I) with a room
contamination load ratio of approx. 1.2 m-1 (contaminated wood
surface/ room volume) was subjected to a ten day long decontamination treatment.
The emission into the ambient air emanated from structural timbers
(half-timbering) and decorative wood (ceiling beams, wall panelling, etc.) with
surface contamination readings ranging from 360 to 4000 mg PCP/kg. Depending on
the point of measurement (window areas with lesser and rear wall area with
higher timber content) the PCP concentration in the ambient air ranged from 1112
to 1186 ng/m3 (22.7 °C) with 792-759 ng/m3 apportioned to
the dust phases. Similarly, for Lindane the ambient air measurements ranged from
220-223 ng/m3 (gaseous and dust phases).
Measurements after the decontamination treatment (23.8 °C) resulted in
significantly lower PCP contamination of the ambient air of 182-367 ng/m3
(71-143 ng PCP/m3 in the dust phase). A similar reduction of the
Lindane contamination of the ambient air could also be recorded (143-150 ng/m3).
As a consequence of these results the scope of the decontamination was
enlarged to include four other rooms. Room I was included again in the second
phase (approx. 205 m3) of the pilot decontamination and the holding
phase was extended to 14 days. A compilation of the test results is given in
Table 1.
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