PRICES include / exclude VAT
Homepage>BS Standards>13 ENVIRONMENT. HEALTH PROTECTION. SAFETY>13.040 Air quality>13.040.20 Ambient atmospheres>BS 1747-12:1993 Methods for measurement of air pollution Determination of the mass concentration of ozone in ambient air: chemiluminescence method
Sponsored link
immediate downloadReleased: 1993-10-15
BS 1747-12:1993 Methods for measurement of air pollution Determination of the mass concentration of ozone in ambient air: chemiluminescence method

BS 1747-12:1993

Methods for measurement of air pollution Determination of the mass concentration of ozone in ambient air: chemiluminescence method

Format
Availability
Price and currency
English Secure PDF
Immediate download
151.20 EUR
You can read the standard for 1 hour. More information in the category: E-reading
Reading the standard
for 1 hour
15.12 EUR
You can read the standard for 24 hours. More information in the category: E-reading
Reading the standard
for 24 hours
45.36 EUR
English Hardcopy
In stock
151.20 EUR
Standard number:BS 1747-12:1993
Pages:12
Released:1993-10-15
ISBN:0 580 22577 1
Status:Standard
DESCRIPTION

BS 1747-12:1993


This standard BS 1747-12:1993 Methods for measurement of air pollution is classified in these ICS categories:
  • 13.040.20 Ambient atmospheres

1.1 General

This International Standard specifies a chemiluminescence method for the determination of the mass concentration of ozone in ambient air.

The method is applicable to the determination of the mass concentration of ozone between 2 µg/m3 [0,001 ppm(V/V)] and 10 mg/m3 [5 ppm(V/V)] at the reference conditions of 25 °C and 101,3 kPa.

Ultraviolet (UV) photometry is specified as the primary calibration method because of its proven accuracy and specificity to ozone. The use of transfer standards is allowed if they have been previously calibrated against the primary calibration method.

1.2 Limitations

The chemiluminescent reaction of ozone with ethylene is not subject to interference from any of the common air pollutants. However, particulate matter, if not removed, will accumulate in the sampling line and may cause a measurable destruction of ozone. If particulate matter is allowed to enter the reaction chamber of the analyser, it will not only scatter the emitted light but will also accumulate on the optical window, thereby causing further attenuation of the emitted light. Also, any nitrogen(II) oxide in the sampled air will to some extent react with the ambient ozone; therefore, the time during which the ambient air remains in the sampling line must be sufficiently short to keep this effect to a minimum.

NOTE 1 It has been reported by some researchers that, at about 80 % relative humidity and 22 °C, the responses for some commercially available chemiluminescence analysers were about 10 % higher than that for dry air. However, comparisons of ambient ozone measurements using commercially available chemiluminescence and UV-photometric analysers showed no significant differences. This suggests that, in practice, any errors associated with calibrations using dry air are compensated by other effects.


Gives a method for continuous or daily measurement of ozone in the range 2Gmg/m3 to 10 mg/m3.