Air Pollution Continuous Monitoring Technology in Japan
Notes on the maintenance and management of automatic monitoring instruments

1. Items related to general air pollution monitoring stations and roadside air pollution monitoring stations

1.1 General matters

1.1.1 Sample collection tube
(1) Materials used for the sampling tube
The materials that constitute the sampling tube should be chosen so that absorption and decomposition of the target substance in the collection tube, and the generation of interfering gas, can be avoided.
With monitoring devices for SO2, NOx, Ox and HC, it is desirable that the collection tube is made of tetrafluoroethylene resin, which has a low absorption characteristic. In the case of CO and SPM measurement devices, the tube of soft vinyl chloride can be used.

(2) Sampling method
a. Individual sampling tube method
The individual sampling tube method is used when the distance of the sampling tube between the sample intake and the monitoring instrument is approximately less than 5 meters. This method installs a sampling tube individually for each of the measurement devices.
As a countermeasure of sampling-tube against rainwater, etc., the funnel attached at its tip should be directed downward. In addition, this method requires a contrivance to avoid the intrusion of rainwater into the station through the sampling tube (See Figure 7.1.1).
Since strong wind could change the condition of the collection tube (in particular, the tip funnel part of the collection tube), always ensure that the collection tube has an appropriate shape.


To make sure that the location of sampling tube into the station is higher than the lowest location of its outside tube.
Figure 7.1.1

b. Manifold method
If the distance of the sampling tube between the sample intake and the monitoring instrument is approximately over 5 meters, the manifold method is used. This method sucks sampling gas through a blower from an intake to the indoors of the station. The collection tubes are made of hard glass and a sample collected by this collection tube is then distributed by tetrafluoroethylene resin, etc. to each of the measurement devices.
It is necessary to pay attention to the air pressure at the intake of the measurement device to avoid negative pressure. A general schematic diagram of its structure is illustrated in Figure 7.1.2.


Figure 7.1.2

Depending on how dirty the collection tube is, it is desirable to clean or exchange it twice a year. When performing this operation, make sure that monitoring instrument are turned off. Otherwise, a generation of a counter-current liquid may occur due to negative pressure. This can lead to a situation where the cleaning or exchange of pipes or liquid becomes inevitable.
The individual sampling tube method allows easy confirmation of defective data caused by dirt in the tube, if a spare tube is prepared beforehand. This method has another advantage of enabling us to bring the collection tube to clean it. After completely removing moisture from sampling tubes, the cleaned tubes should be preserved so that they will not be dirtied. With the manifold method, since the tube is made of hard glass, the tube can be easily damaged when cleaning it. Another defect is to need the long time for the maintenance.

Contents Other Databases GEC Homepage