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Udvikling af sporgasmetode til brug for måling af transport af forurening mellem
renserier og tilstødende lejligheder - laboratorieforsøg
English Summary
The Danish Environmental Protection Agency has initiated a project aimed to develop and
test a tracer gas method that allows long-term measurements of air movements in the
environment with high background concentrations of organic compounds. The method is
primarily aimed at measurements in cleaning establishments and above-lying apartments.
The development project is divided into three phases whereof this report describes the
initial phase. The aim of the first phase is to develop and test a measurement and
analysis method under laboratory conditions.
If the initial phase is successful the intention is to follow-up with a number of field
testing (phase 2) and measurements in existing cleaning establishments (phase 3).
Laboratory experiments have been aimed at designing a method and determine a limit of
detection, capacity, length of measurement period, precision, and uncertainty among other
things for the method.
The development work is based on the PET method for air exchange measurements developed
by Statens Byggeforskningsinstitut (the Danish National Building Research Station). The
project has indicated that it is possible to modify the PFT method making it applicable in
situations known from the cleaning establishments where the background concentrations of
organic compounds in the air are significantly higher than the tracer gas concentration.
The modification consists of the following:
 | Change of sampler type to a carbon based monitor |
 | Change of desorption principle from a thermal desorption to liquid desorption |
 | Change of detector type from ElectronCaptureDetector (ECD) to mass specific detector
(MS) |
The chromatography and the analytical limit of detection were investigated at a number
of preliminary tests with analysis of liquid standards. It turns out to be possible to
detect and separate tracer gasses and cleaning fluids despite the large differences in
concentrations. The analytical limit of detection is determined to be 0.03 µg (total
amount per sample).
The testing of the method in form of sampling and analysis was carried out by exposing
the samplers to realistic concentrations of cleaning fluids and tracer gasses in a dynamic
gas generation system. The tests were carried out for two sampler types (Radiello and 3M
type 3500) and for two cleaning fluids (tetrachloroethylene and hydrocarbons mixtures).
Perflouromethylcyclohexane (CAS no 355-02-2) and perflouro-1,3-dimethylcyclohexane (CAS
no 335-27-3) were applied as tracer gasses. The compounds are often mentioned by name of
PP2 and PP3 respectively.
The concordance between the theoretical and experimental determined uptake-rates is
more than 80% improved with a single exception for the 3M samplers. The theoretical
determined value is calculated from tracer gasses' diffusion coefficients in air.
This is assessed to be satisfactory and within the expected compared to other
investigations of experimentally identified and calculated values. The experimentally
identified uptake-rates for the two samplers appear from the report and should be used at
prospective use of the method.
The relative standard deviation for the specific uptake-rates is in the order of 10%.
The project has indicated that the method's capacity allows measurements for up to
fourteen days without the sampler displaying any signs of saturation.
With tracer gas concentrations of 15 µg/m3 in the cleaning establishment
the method's limit of detection will be able to detect concentration reductions of up to a
factor 1000 in the above-lying apartments at measurements exceeding fourteen days.
An assessment of health risks at the projected tracer gas concentrations has been
carried out. The assessment has been carried out based on existing data sheets and
information in a number of reference works and databases. The Danish Environmental
Protection Agency's has supplemented with a toxicological assessment of the tracer
compounds. The effected assessments indicate that a concentration of 15 µg/m3
hardly poses a risk for the people on the premises.
No conditions assessed to be critical to the continued development of the method have
been detected during this phase. The second phase of the project implementation of
a number of field tests can therefore be initiated.
In connection with the implemented laboratory tests circumstances that should be
included and clarified during the coming phase have turned up. It is concerning an
assessment of possible sink effects significance for tracer compounds. Coming phases
should also include Rynex cleaning establishments in the testing of the method.
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