PAPER 12. CONTINUOUS MEASUREMENTS OF AIR INFILTRATION IN OCCUPlED DWELLINGS P.F. COLLET. Technological institute Denmark

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PAPER 12 CONTINUOUS MEASUREMENTS OF AIR INFILTRATION IN OCCUPlED DWELLINGS P.F. COLLET Technological institute Denmark

Continuous measurements of air infiltration in occupied buildings The measurement system, developed by the Institute of Technology at TBstrup, Denmark, is a microcomputer-controlled system for registering air change rates using tracer gas according to the constant concentration method. The system is designed for measuring and metering tracer gas in up to ten separate rooms. The air change rate to outdoors is measured on the basis of the amount of tracer gas supplied to maintain a constant concentration. The system operates through automatic data logging on a floppy disc and can run without supervision for extended periods (up to six days). Background ------------ In conjunction with energy saving measures, both in existing buildings and in new buildings, there is a natural desire to build as airtight as possible. There has been a considerable amount of measurement of natural ventilation in buildings in Sweden and Denmark but such measurement has been of instantaneous values where outside doors, windows etc have been closed. This does not give any indication of the air change rate when the building is occupied, ie when the occupants open and close windows, go in and out of the building etc. The prerequisite for being able to measure a building's airtightness in relation to a: the building's air change rate when occupied b: the building's content of gases and allergens c: the building's energy consumption is being able to measure the true air change rate over an extended period (1-2 weeks) while the building is occupied. As an example, one could expect that the reason for the differences in formaldehyde concentration in the air and air change rates in Swedish and Danish investigations could be attributed to air change rates not being measured while the building is occupied. Correspondingly, it can be shown that by making the building tighter, the frequency of the occupants opening windows etc increases so that the effective air change rate is greater than that demanded by the tightness. Thus there is a real risk of increasing the air change rate instead of reducing it.

Design of the system... The measurement system comprises a central unit in which the dosage, control and measurement units are housed (see figure 1). From the central unit, 2 hoses go to each of the measurement rooms. One hose is used for dosing the gas while the other is used for collecting room air for central concentration control. The dosing unit: The dosing unit comprises a bottle of tracer gas (N O), 10 solenoid valves, 10 2 metering jets and a pressure gauge. The dosage to individual rooms is determined by two parameters: 1. The pressure in the jet. 2. The opening period of the solenoid valve. To be able to calculate the flow through the jet simply and satisfactorily, the pressure and the jet size are selected so that there is an over-critical flow in the jet's smallest cross section - "the mill". At an over-critical flow, the maximum possible velocity in the mill is the speed of sound. Over-critical flow is achieved when the ratio between the available pressure and the exit pressure at the jet exceeds approximately 1.9. When increasing the available pressure in excess of this ratio of 1.9, the mass flow is proportional to the available pressure and independent of the exit pressure. In other words, when there is over-critical flow in the jet, the mass flow varies linearly with the pressure at the input side (the pressure used is in the region of 3 bar). The room is dosed every 30 seconds. The dosage time can vary between 0 and 30 seconds but is set so that the minimum dosage is 2 seconds. The jets used (see figure 3) have a very fine quadratic characteristic. 10 x 2 second doses provide the same amount of gas as 1 x 20 second dose. The measurement unit: The measurement unit comprises 10 3-way solenoid valves, a Uras 7 n infrared gas absorption detector and a gas suction pump. The concentration of N20 in the room air is measured with the aid of a two beam infrared gas absorption detector (see figure 6), and the measurements are expressed as the difference between the absorption of light in the two beams. The reference cell contains nitrogen, which does not absorb light in the measurement range of the detector. The measurement cell contains the gas to be measured.

A single measurement takes 30 seconds. Thus if 10 rooms are connected, the tracer gas measurement in the rooms can be determined every sixth minute. There are two components in the room air in addition to N 0 that absorb light in the detectorxs measurement range. The effect of C?02 is removed by inserting a filter in Uras and the effect of moisture in the air is eliminated mathematically. In order to get "fresh air" in the measurement apparatus a pump is installed which pumps from the hoses not used in the measurement process. To eliminate drift at the 0 point, a test gas with a 50 ppm N 0 concentration 2 in N2 is measured at fixed intervals. The measurement apparatus's 0 drift point is corrected mathematically. Control and registration unit: A microcomputer is used as a control and registration unit (SORD MARK 11). Results -------- The results of one day's measurements in a house are shown in figures 4 and 5. The house is of a timber construction on two floors located in i(qge. Measurements were taken in all rooms while in use. - Room number 1 2 3 4 5 6 7 8 Description Living room Kitchen Hall Bathroom Stair well Bedroom Room WC Volume Window open Mixing fans 84m 22 m 3 9m 3 9m 3 32 m 3 25m 3 38m3 7m 3 No No No Yes Yes No To 3 Yes No No Yes Yes? Yes No

The greatest problem encountered during measurement is maintaining a constant concentration of N 0 in rooms. 2 Different conditions limit the extent to which the concentration can be regulated: 1. The facility for mixing air in the room. For example, in bedrooms it is not possible to use mixing fans for mixing the room air at night. 2. The rooms are measured at fixed intervals of up to 6 minutes. If a window or door is opened, a certain time elapses before this is registered. The discontinuation of strong ventilation can result in an extended period of increased concentration in a room. Figure 2 shows the result of a trial using two different types of control. momentary concentration of N 0 was measured every minute. 2 The Further... development of the measurement system Futher endeavours to improve the system will be to register temperature and moisture content in parallel with air change rate measurement. This will provide a better illustration of the indoor climate and will permit continual monitoring and correction of the effect of moisture on the URAS 7n. We also hope to improve the dosage procedure so that even small rooms with a considerable air change rate can maintain a stable concentration of N 0. 2

I Computer I Uras sample: Computer off FIGURE 1

Design of the measurement apparatus, principle Metering hoses Pump Collection FIGURE la

To pump through needle valve From room Critical orifice Dose to room FIGURE 3

FIGURE 4: Tracer gas concentration la1 whole house PPM GFILGEBFIKKEN MRRK 4.4 DEC 1981 0 4 8 12 16 20 0 4 8 12 16 20 0 TIME 14 15 DRG (bl individual room PPM GFILGEBFIKKEN MFlRK 4.4 DEC 1981 -.-.-RUM 9 ------- RUM 8 -.--.-.. RUM 7 ----RUM 6 ------ RUM 5 -.-.-.-.-. RUM 4 ------ RUM 3 --------- RUM 2... RUM 1 0 4 8 12 16 20 0 4 8 12 16 20 0 TIME 14 15 DRG

FIGURE 5: Ar change rate (a) whole house I'VH GRLGEBFIKKEN MFIRK 4. 4 DEC 1981 - HUS TIME DRG (b) individual room IYM GRLGEBRKKEN MFIRK 4.4 DEC 1981 -.-.-RUM 9 ------- RUM 8 RUM 7 ----RUM 6 ------ RUM 5 -.-.-.-.-. RUM 4 ------ RUM 3 --------. RUM 2... RUM 1 TIME DFIG

Basic diagram of the infrared gas analyser Uras 7 N Receiver Condenser diaphragm Counter electrode Receiver shutter Fi 1 ter cell Direct voltage source Measuring cell Analysis chamber Reference chamber High-impedance resistor Radiation sources Shutter wheel Shutter wheel motor Amp1 ifier Mains stabilisation FIGURE 6

Measurements taken while house was occupied on 10-11 September 1981 between 10.00 and 11.00 Average ppm N20 concentration per hour Location: Ringstedvej 20 FIGURE 7