BACKGROUND
[0001] Ventilation measurement in its most general form implies measuring the supply rate
of ambient air to a building and how this air is distributed within the building space.
[0002] Field measurement of ventilation can be performed with several known techniques.
The most commonly used technique involves measuring the air flow rates in the ventilation
equipment, ducts or supply- and exhaust devices. Such ventilation measurements can
only be used in mechanically ventilated buildings. The methods also have some additional
limitations:
- Estimated air flows may be a mixture of ambient air and air which has previously circulated
in the building (return air or air short-circuiting in ducts and heat exchangers).
- Ambient air is also often infiltrated into the building through other routes than
via ducts (windows, leakage etc.), a contribution which is neglected in measuring
in ducts and supply- and exhaust devices).
- No information is gained on how the supplied air is distributed within the building
space, after it has left the ductwork or the supply devices.
[0003] In order to be able to measure the ventilation rate in buildings in which the supply
of air wholly or partly occurs in other ways than by mechanical ventilation, one has
to rely on tracer gas technique. Depending on which ventilation parameters are of
interest, several different tracer gas techniques are available. Some of the most
commonly used techniques are shortly described below.
[0004] The concept "ventilated system" involves all spaces, that are somehow connected in
a ventilation sense, i. e. all spaces to which or from which air can be transferred
from or to other parts of the system. The only air which can be supplied over the
boundary of a ventilated system is ambient air.
1- DECAY TECHNIQUE
[0005] A tracer gas is mixed into all spaces of the ventilated system to the same initial
tracer concentration, after which the decay as a function of time is registered in
one or several points. Different ventilation parameters can be calculated from the
decay course. Some different cases can be separated.
1a) Measurement of the specific ventilation flow rate
[0006] (previously called air change rate). In this case it is required that a thorough
mixing is maintained in the whole system with the help of for example fans. The tracer
gas concentration curve as a function of time will then ideally show an exponential
decay. Evaluation of the specific ventilation flow rate is usually obtained from the
slope of a plot of the logarithm of concentration versus time.
[0007] In many cases (especially when there are very large rooms or many rooms) it is difficult
to achieve a satisfactory mixing. The decay will in that case not be entirely exponential.
In the evaluation of the air change rate it is then common to utilise only the last
part of the logarithmic decay curve, which usually is linear. This procedure is an
approximation and a fairly good skill is required, in order to measure at the correct
positions and judge what part of the decay curve is useful.
1b) Measurement of the local mean age of air.
[0008] Also in this case, tracer gas is mixed to an even concentration in the whole of the
ventilated system, but during the measurement of the decay, no effort is done to influence
the mixing in the system. In this case different decay curves are usually obtained
in different parts of the system, which reflects the different distribution of ventilation
air. Well ventilated parts of the space shows a quicker decay than badly ventilated
parts. The evaluation is done by measuring the area under the plot of concentration
versus time from the beginning of the decay until all tracer gas has disappeared from
the system. This area (integral) constitutes a direct measure of the mean age of air
at the measuring point. The local mean age of air tells how long the air around the
measuring point in average has stayed in the building, since it entered as ambient
air. By measuring the decay at several positions in the system, it is possible to
map the distribution of ventilation air. Spaces mainly ventilated with direct supply
of outside air, show a shorter mean age than such mainly ventilated with air from
other spaces.
[0009] The local mean age in the exhaust air is always equal to the inverted value of the
specific ventilation flow rate. When it is possible to measure in the exhaust air
this method makes it possible to determine the air change rate, even if the system
is badly mixed.
2. CONSTANT EMISSION TECHNIQUE
[0010] In this case, tracer gas is injected into the system with a constant rate. After
some time the concentration of tracer gas and its distribution in the system will
attain a steady state. Also in this case some special cases can be distinguished.
2a) Determination of total ventilation flow rate
[0011] In this case the whole system shall be mixed by means of fans, so that the tracer
gas concentration is equal everywhere. The evaluation is performed by measuring the
steady state concentration and from that value calculate the total ventilation flow
rate as the quotient between the rate of tracer gas emission and the tracer gas concentration.
[0012] When it is possible to measure in the exhaust air it is always possible to determine
the total ventilation flow rate from the mentioned quotient, even if the system is
badly mixed.
2b) Determination of the local mean age of air.
[0013] Also in this case tracer gas is spread with a constant rate, but the emission is
to be evenly (homogeneously) distributed in the whole space of the system. This technique
(the homogeneous emission technique) is relatively new and is practically performed
by dividing the system space in smaller zones, in each of which tracer gas is emitted
with a rate, which is proportional to the volume of the zone. The equilibrium concentration
in a zone is a direct measure of the local mean age of air (= concentration divided
by the emission rate per volume unit). By measurement of the concentration in many
parts of the system, it is possible to map the distribution of the ventilation air.
[0014] If it is possible to measure in the exhaust air, the specific ventilation rate of
the system can be calculated from the inverted value of the mean age of air at that
point.
2c) Determination of air flows between zones.
[0015] By using several different types of tracer gas simultaneously (e. g. different tracer
gases in the different zones in a zone-divided system) all air flows to and from each
zone can be calculated. Such multi-tracer gas technique is relatively seldom used
in research and field measurements). With the so-called passive tracer gas technique,
simultaneous use of 2-3 different tracer gases is relatively common.
3. CONSTANT CONCENTRATION TECHNIQUE
[0016] This technique can be used in a zone-divided system and implies that an automatic
dosing device injects tracer gas to the different zones, in a way that all zones achieve
the same tracer gas concentration. The technique requires a relatively complicated
equipment, with feedback between the measured tracer gas concentration and the injection
rate. The direct supply of ambient air to each zone can be estimated in this way.
4. PULSE TECHNIQUE.
[0017] This is a relatively unusual technique, which is sometimes used in larger buildings
with mechanical ventilation. A certain amount of tracer gas is injected into the supply
air and the time response of the concentration is measured in the exhaust air. The
total ventilation flow rate can be calculated from the injected tracer amount, divided
with the integral under the concentration response in the exhaust air. From the "first
moment" (the integral of the product of concentration and time) for the concentration
plot, the local mean age of air can be determined.
Problems with field measurements
[0018] The method, which this invention refers to, is meant to facilitate ventilation measurement
with tracer gas in field work. I will therefore shortly describe the problems of applying
the different known techniques in field work and demonstrate how the new invention
can solve these problems.
[0019] All techniques require analysis of (low) concentrations of tracer gas. Sampling equipment
as well as tracer gas analysis equipment is therefore needed. Accurate tracer gas
devices are expensive equipment, which has to be handled by experts. The expensive
tracer gas equipment as well as the expertise are tied up during the time period,
during which measurements are made. It is therefore out of question that tracer gas
measurement with analysis equipment in the field can be commonly used in field work.
[0020] One solution to this problem has been to take air samples in the field (with bag,
syringe etc.) and bring the samples to a laboratory for later analysis and evaluation.
In order to be able to make accurate evaluation of the decay technique, several samples
taken with a time delay at each sampling position are necessary. In order to get a
correct equilibrium value with the constant emission technique, first a long waiting
period is necessary after which several samples must be taken.
[0021] The air mixing constitutes a special problem with method 1a and 2a. Artificial mixing
is impractical in occupied premises.
[0022] In recent years the so called passive tracer gas technique has grown in use. In this
technique tracer gas is spread with a constant rate through diffusion from miniature
containers, which have been positioned in the measurement object. Small diffusive
air samplers are also positioned at suitable locations in the measurement object.
The samplers accumulate tracer gas from the air with a rate which is proportional
to the concentration. After the measurement period (from a few days to months) the
samplers are sent to a laboratory for analysis of the accumulated amount of tracer
gas. One advantage with the passive tracer gas technique is that staff is only needed
for positioning the equipment and that no expensive equipment is tied up during the
measurement. The technique is used for determining the total ventilation flow rate
according to technique 2a, and since some time also for determining the local mean
age of air according to 2b, as adjustable passive tracer gas sources have been available.
Some investigations are also performed according to 2c.
[0023] This passive tracer gas technique has many advantages for field measurements. It
yields among other things the average ventilation performance during an extended time
of normal occupancy. This technique can however occasionally be less desired. One
such occasion is when a short term measurement is desired, for example during a working
day, due to the fact that the ventilation may be decreased during off-work time. Another
occasion is when it is desirable to have the ventilation measurement rapidly and non-expensively
concluded, for example for a routine check of the ventilation performance, in which
case it is allowed to accept a value, which is less representative for an extended
time period.
[0024] It is problematic to make quick measurements with the passive technique. The air
sampling shall namely be performed during "steady state conditions". If the air has
a mean age of 2 hours or more (which is normal in dwellings), it is a delay of 8-10
hours to approach this state after positioning the tracer gas sources. When measuring
extended times, this build up period can be neglected, but with short term measurement
it is of essential importance. The samplers must not be opened before a considerable
time period has elapsed, which complicates the handling.
[0025] The invention solves these problems.
[0026] The manner to investigate the ventilation with tracer gas technique according to
the invention is defined by the features of claim 1.
[0027] Due to the fact that the integrating samplers are active already from the beginning
of the tracer gas emission, the spreading of tracer gas in the different zones may
be performed in any pace, which is convenient. Any time delay between the injections
into the different zones is without importance. The integrating samplers should have
the characteristics, that their rate of tracer gas sampling is directly proportional
to the concentration of trace gas in the air. This is essentially true for samplers
of the diffusive type and for all "pumped" sampling.
[0028] After the sampling the samplers are inactivated and sent to a laboratory for analysis
of the amount of sampled tracer gas (M).
[0029] Knowing the "equivalent air sampling rate (κ)" of the samplers the integral:

can be evaluated, from which the local mean age of air

can be calculated

where m/V is the amount of injected tracer gas per volume unit of the space.
EXAMPLE
[0030] Below, an example is given of how a ventilation measurement may be performed, using
the methodology, for which a patent is applied. The example should not be regarded
as a limitation of the general character of the patent.
a) An inspector is visiting a naturally ventilated dwelling, in which the ventilation
and the distribution of ventilation air in the different rooms are to be estimated.
In each room the inspector mounts an open diffusive sampler on the wall at a height
of 1.7 m.
A diffusion sampler may consist of a 5 cm long glass tube with an inner diameter of
4.3 mm, closed in one end. In the glass tube there is an adsorbent bed with approx.
100 mg activated charcoal, which extends from 17 mm below the open end of the tube.
Through diffusion the constituents of the air are transported through the open end
of the glass, down to the adsorption bed, in which most contaminants in the air, including
the tracer gas are adsorbed. The sampling rate of tracer gas is determined from Fick's
first law of diffusion, which implies that the sampling rate is directly proportional
to the concentration of the compound in the air, if the adsorption is 100% effective,
which is generally true for small amounts of adsorbed compounds. The activated charcoal
in the sampler retains all, which is adsorbed and the diffusion sampler therefore
functions as a integrating sampler, which means that all amounts are added on the charcoal.
b) The controller then visits the different rooms, in which he estimates the volume
of the room space and adjusts the tracer gas injection equipment in such a way that
he can deliver an amount of tracer gas, which is adjusted to the room volume in a
pulse. After the tracer gas pulse, he slightly mixes the tracer gas into the room
air, whisking with a piece of paper board. When he has finished all rooms this way,
he presents a return envelope to the occupants together with instructions to seal
the sampling tubes after approx. 20 hours, use the enclosed plastic caps, put the
samplers in the envelope and post it to the laboratory.
The tracer gas may be of the perfluorocarbon type, which are non-toxic compounds,
which have the property of not being adsorbed on commonly occurring indoor materials
and that they can be analysed at extremely low concentrations. The total amount injected
in a dwelling is less than a thousand of a gram.
c) The laboratory receives the labelled samplers and transfers the activated charcoal
to a sampler flask, into which a millilitre of solvent is also added. The solvent
extracts the adsorbed compounds from the charcoal. A small portion (a microlitre)
of the solution is then injected, by means of an automatic device, into a gas chromatograph
for separation and analysis of the tracer gas amount in the sample.
Gas chromatography is a separation technique, based on the fact that different compounds
are transported with different speed through a capillary column which may have 0.2-0.5 mm diameter and 5-50 m length. A
carrier gas, which is flowing through the capillary column carries the compounds injected into it. The adsorption of the compounds on the column wall
delays the different compounds different times, so that the compounds leave the column
on different times after injection. After the separation column there is a so-called
electron capture detector, which has special sensitivity for the tracer gas (in this
case fluorinated hydrocarbons). The output signal from the detector is depending on
the amount of tracer gas passing, which allows the amount to be calculated from a
calibration plot.
d) From the analysed amounts, the local mean ages of air can be calculated for each
sample in the points at which the sampling were made, according to the equation stated
earlier. Besides the analysed amount, it is necessary for the calculation to know
the air sampling rate for the sampler (known from calibration) and the injected amount
of tracer gas per volume unit in the measurement object (reported by the controller).
Thereafter, the laboratory writes a report to the controller.
[0031] The term "zone" used above and in the claim may be equivalent to a "room" in premises
or dwellings but must not be so.