Figure 6.7 shows that certain categories of volatile organic compounds
(VOCs) are easily transferred by a sorption transfer mech anism. Among the
tested VOCs, those having the highest boiling point were best transferred. The
largest transfer rate in a well-installed unit was found for phenol (30 per cent).
Leakage and pollutant transfer can be avoided or at least strongly reduced
through proper installation of the wheel, good maintenance of the gasket,
proper installation of a purging sector, and by maintenance of a positive
pressure differential from supply to exhaust duct at wheel level.
Coils
Laboratory tests (Bluyssen et al., 2003) show that heating and cooling coils
without condensing or stagnating water, are components that have small contri-
butions to the overall odour intensity of the air. On the contrary, cooling coils
with condensed water in the pans are microbial reservoirs and amplification
sites that may be major sources of odours to the inlet air.
Measurement protocols
HVAC systems are in general low sources of measurable chemical pollutants .
When searched for, most pollutants are below the detection limits of
common analysers, and chemical analyses can be successful only in very
polluted systems. They are therefore not discussed here.
No standard procedure exists for microbiological measurements in ventila-
tion systems. The techniques used are air sampling with impactors, gluing
airborne microbes (mould, yeast, bacteria) on appropriate culture media, or
simply exposing these culture media in open Petri dishes or on films lying or
glued on the inner walls of ducts or units. The main problem is ensuring
reproducible samples.
Only two methods are presented here: the measurement of sensory pollu-
tion and the assessmen t of contaminant transfer.
Sensory pollution
Principle of the method
Since the nose is the most sensitive instrument to detect pollutants, the
measurement protocol to assess the pollution resulting from ventilation systems
or components is mainly focused on measuring the sensor y pollution effect,
evaluated by a trained panel of people (Bluyssen, 1990; Elkhuizen et al., 1995).
A panel of 12–15 subjects is selected and trained to give a value to the odour
intensity. To evaluate air quality at a given place, each panel member smells the
air – after having refreshed his or her nose in pure, fresh air – and gives a value
to the odour intensity. The final value is the average over the panel.
Contaminants in Air Handling Units 113
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