Technical Publications
Theoretical and Practical Considerations in the Use of
Wind Tunnel for Odour Emission Measurement
Lawrence Koe, Yih-Ming Koh, Chuck Schmidt, Jay Witherspoon, Tom
Card, Yan Wu
EXECUTIVE SUMMARY
In the past decades, wind tunnel systems have been commonly used
for aerodynamic research including simulation of wind loads on
buildings, automobiles and airplanes. In recent years, this methodology
has been deployed for measurement of odour emission rates from
area sources such as primary sedimentation tanks at sewage treatment
plants. The size of the wind tunnel used for this purpose is much
smaller than conventional wind tunnels. Emission rates obtained
from such measurements have been reported to differ by up to 300
times, compared to the conventional flux chamber sampling method.
Thus, it is important to provide a review of the system.
In this paper, the basic principles and theories used in a conventional
wind tunnel system is presented and the pertinency of these theories
to a small-scale wind tunnel system is discussed. It has been
found that while the theories are generally applicable to a small
wind tunnel system, there exist some limitations that may give
rise to errors in odour emission rate measurement, especially
under field conditions. Deployment of wind tunnel system onto
a moving area surface may upset the development of boundary layers
in the system, leading to erroneous measurement of odour emission
rates. A lack of understanding of the effect of upward rising
air bubbles on the dynamics of flow in wind tunnels limits the
application of wind tunnels for area sources with outward flows
such as aerated area sources. High detection limits of wind tunnel
systems also pose a problem in measuring odour emission rates
from area sources with low odour emissions.
Comparisons between wind tunnel and flux chamber technology is
presented. Compared to a flux chamber, wind tunnel technology
is not as commonly used worldwide. Though wind tunnels may be
used to simulate emissions under normal ambient conditions by
having results that are scaleable, no clear documentation has
been provided for these adjustments. There is also a general lack
of information and documentation on issues regarding the sampling
protocol for a wind tunnel system and peer reviewed papers that
support the accuracy or recovery rates of the system. Whereas
the flux chamber technology is a commonly accepted direct measurement
technique available for various odour sources including open wastewater,
solids surfaces as well as aerated surfaces.
Field measurements have revealed that the results obtained using
a wind tunnel were much higher than those obtained with a flux
chamber. It has been observed that during the sampling session,
the inside of the wind tunnel was undergoing a wave condition.
This artificial wave condition may bias the measured odour fluxes
and yield results that are upward relative to those measured by
a flux chamber.
Practical issues have also been considered and discussed. Deployment
of wind tunnel sampling systems involves the use of bulky and
cumbersome equipment and accessories. Some accessories are also
found to be heavy. This may result in additional time for system
assembly and manpower for equipment handling. Due to these problems,
cost effectiveness of the technology becomes an important issue
that must be considered before deploying the technology for odour
sampling and emission measurement.
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