7.9 Appendix 9. RAE Systems Contacts .......................................... 133
Table Of COnTenTs
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1. INTRODUCTION
WARNING
The products described herein will perform as designed only if they are
used, maintained, and serviced in accordance with the manufacturer’s
instructions. Failure to use, maintain, and operate products properly can
result in dangerously inaccurate readings.
INTRODUCTION
CAUTION: For safety reasons, the equipment described here-
in must be operated and serviced by qualied personnel only.
Read and understand this instruction manual completely before
operating or servicing.
ATTENTION: Pour des raisons de sécurité, ces équipments
Doivent être utilisés, entretenus et réparés uniquement par un
personnel qualié. Étudier le manuel d’instructions en entier
avant d’utiliser, d’entretenir ou de réparer l’équipement.
Custom Tubes
Please contact RAE Systems about the availability of custom tubes not
included in this handbook. Contact information is included on page 128.
Application & Technical Notes
RAE Systems’ web site includes the Application Notes and Technical
Notes cited in this handbook, as well as many others. Visit our web site at:
www.raesystems.com.
This handbook describes the use and performance of gas detection tubes and
sampling pumps manufactured by RAE Systems Inc. RAE Systems began
manufacturing gas detection tubes in 1997 and is adding many new tubes to
its product line each year. Modern production facilities and techniques allow
us to offer high-quality tubes at a highly competitive price.
Gas detection tubes were rst developed at Harvard University in the early
1900s for measuring carbon monoxide. In this method a gas sample is
pulled through a glass tube containing a reagent, and a reaction between
the gas and solid reagent forms a color that is related to the concentration
of the gas. The concept is similar to other colorimetric methods such as pH
paper for measuring acids and bases, and bleaching of dyes to determine
ozone or chlorine levels in water or air. Early tubes were designed mainly
for conned space entry, such as in the mining industry, where CO and
H2S are the main toxic gases. Since then, a large number of tubes
have been developed for a broad range of chemicals. With the coming
of OSHA regulations in the workplace in the 1970s, these compounds
have expanded from mostly inorganic, acutely toxic compounds to include
a large number of organic compounds whose health effects tend to be
more long term. Along with this change has come an increased need for
specicity in the measurements.
A few important factors limited the accuracy of early tube/hand pump systems.
First the tubes had no precalibrated markings. Some tubes were read using
a color comparison chart, which depended on the user’s interpretation of the
color. Other tubes came with an external scale that was slid into position by the
user. This introduced potential error in the position of the scale but, more important, did not allow for variations in the length of stain produced by different
batches of the same tubes. Modern tubes avoid such errors by having calibrations performed on each batch, which are then marked directly on the tubes.
A second error source was in the volume of air sampled. Early pumps were
variations of a rubber squeeze bulb that gave poor reproducibility in the
amount of compression. Later, xtures were added to the bulbs to ensure
a uniform compression and thus a xed volume. The Draeger and MSA
bellows pumps function in the same way as the squeeze bulbs, but draw in
accurate sample volumes.
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Air sampling can also be performed using piston pumps, which latch into
a precisely dened position to x the volume. These pumps pull a strong
vacuum initially and thus create substantially higher owrate than the
bellows pumps. Piston pumps generate a high ow initially followed by
an approximately exponential decay, whereas bellows pumps provide a
more steady ow initially followed by the slow decay. The difference in ow
patterns means that the pumps cannot be interchanged between types.
For example, piston pumps sometime cause a smearing of the color stain
INTRODUCTION
when used on tubes originally developed for bellows pumps. This occurs
because the higher ow rates do not allow enough contact time to give
sharp endpoints when a piston pump is used.
For a period of time, attempts were made to improve accuracy by stabilizing
the ow rate using rate-limiting orices. Some manufacturers supplied
as many as four different orice sizes to match the particular tube being
used. However, exchanging limiting orices proved to be cumbersome
and unnecessary as long as enough contact time was allowed to avoid
smearing the stain. Therefore, limiting orices have fallen out of use and
it has now become standard practice to build the ow restriction into the
tube itself. This is done by selecting the particle size of the support material
and type of end plug that give a sampling time appropriate for the particular
chemical reaction of the tube.
2. QUALITY ASSURANCE PROCEDURES FOR
GAS DETECTION TUBE MANUFACTURE
All RAE Systems gas detection tubes are developed in an ISO 9001
certied facility and manufactured in an ISO 9001 certied factory. All
procedures, work instructions, and quality records are documented and
maintained to ensure tube quality. The procedures are outlined below.
A. Tube Selection. Glass tubing is selected to t a standard bore size to
ensure uniform length of color change.
B. Support Preparation. Silica, alumina, and other support materials
are chosen from the highest quality available and sieved to yield a
narrow particle size distribution. The supports are then further puried
as necessary and dried to well-dened levels depending on the
requirements of the tube reactions.
C. Reagent Loading. Chemicals are chosen according to strict purity
standards and loaded onto the support materials. Deposition of the
chemicals onto the support follows a protocol developed specically
for each tube type. The loaded support material is then dried as
needed for the reaction.
QUALITY ASSURANCE
As a result of these developments, modern tube/pump systems have
stabilized into two categories: (1) low-vacuum bellows pumps with less
ow resistance in the tubes, by virtue of being wider (~7 mm o.d.) and
having larger particles, and (2) high-vacuum piston pumps with greater
resistance in the tubes by being narrower (~5 mm) and having smaller
particles. The bellows pump/tube systems tend to have faster sampling
but require more pump strokes to complete a measurement, whereas the
piston pump systems generally need fewer strokes but longer sampling
time per stroke. RAE Systems tubes are primarily of the narrow-bore type
and are designed for use with a piston sampling pump.
4
D. Tube Filling and Sealing. End plugs are selected of materials that
do not react with the reagent. The tubes are lled under conditions
that minimize exposure to air, water vapor, or other gases that may
affect the quality of the tubes. The tubes are then packed tightly by
a combination of shaking and physical compression. The ends of the
tubes are then melted closed using an automated ame sealer. Any
necessary inert atmosphere is maintained through the tube-sealing
process.
E. Calibration. Each batch of tubes is calibrated independently of other
batches. A series of standard gases are purchased or prepared by a
variety of methods, including ow dilution of gas primary standards,
permeation tubes, and diffusion tubes, or static dilution from liquid or
gas primary standards. Multiple tubes are used to determine each
calibration position, and these are then printed onto each tube in the
batch with an automated printing machine.
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F. Packaging. The tubes and their technical data sheets are packed
into labeled boxes with protective corrugated cardboard.
G. Quality Control Sampling Plan. A portion of each batch is sent to
the RAE Systems Quality Assurance Laboratory for independent QA
testing. The most widely used tubes pass the accuracy criterion of
≤±15% of length of stain. A separate set of tubes is stored in the QA
laboratory and the manufacturing facility for evaluation at later dates,
if necessary.
3. OPERATION OF DETECTION TUBES & PUMPS
CAUTION:
Wear safety glasses and gloves when opening
tubes or handling open tubes with sharp edges.
Failure to wear protective equipment may lead to
cuts and other severe injuries to eyes and hands.
H. Accuracy and Precision. The accuracy is measured by testing
at least ve tubes and calculating the average deviation from the
standard gas value. The precision is calculated as the standard
deviation from the average value of the ve measurements. All tubes
meet the accuracy and precision criteria listed in Table 2-1:
Table 2-1. RAE Systems Tube Accuracy and Precision Specications
using it for a series of measurements. Failure to
test the pump for leakage may lead to dangerously
inaccurate readings.
Avoid contact with tube contents in case of
accidental breakage. Exposure to tube contents
can result in signicant health hazards.
Dispose of spent tubes according to local
regulations. Review the reaction principle and
other information listed in the Gas Detection Tube
Data Sheet supplied to identify materials that may
require special disposal procedures. (Data Sheets
for all currently available RAE Systems tubes are
included in Chapter 5.)
OPER ATION
I. Interim Storage. Only batches that pass all quality assurance
procedures are sent to interim storage, where they are maintained at
3-7°C (37 - 45°F) in darkness until shipment.
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3.1 Hand Pump Description
strokes is indicated on one side, along with the total sample volume, the
unit of measure, the gas type, and the batch number.
2. Data Sheet. Each box is packaged with a Data Sheet that provides
detailed information on the tube performance. Figure 3-3 is an excerpt
of a typical data sheet. Complete data sheets are provided in Chapter
5 and discussed in detail in Chapters 4.2 and 4.3.
Figure 3-1. LP-1200 Hand Pump with tube inserted.
The LP-1200 is a piston-type hand pump that draws a xed volume of
gas, selectable at either 50 mL or 100 mL by rotating the handle. A tight
vacuum seal is formed by a greased plunger gasket. The tapered rubber
inlet accommodates a range of tube diameters for different types of tubes.
The inlet lter prevents glass pieces and dust from entering the shaft. An
end-of-ow indicator in the handle turns white when the gas sampling is
complete. A pump stroke counter is rotated to keep track of the number
of strokes completed.
3.2 Tube Measurements
3.2.1 Tube Description & Packaging
OPER ATION
1. Tube and Box. Figure 3-2 shows the key components of a RAE
Figure 3-2. Gas detection tube parts description.
Top: Standard single tube. Bottom: Pretreatment tube
connected to measurement tube with rubber connector.
Systems gas detection tube. The tubes are typically packaged in a box
of 10 tubes. Each box has quick instructions on the back. Some tubes
require preconditioning of the gas and are packaged with 5 pretreatment
tubes and 5 measurement tubes for a total of 5 measurements. The
concentration scale is printed on the tube and an arrow indicates the
direction in which the gas must enter. The standard number of 100 mL
Gas Detection Tube Data Sheet
Hydrogen Sulde H
Extended
Range
Range (ppmv)12.5 - 125
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor (CF)
Figure 3-3. Excerpt of a Tube Data Sheet
3. Part Number. The 7-digit part number is indicated on the top right of
the data sheet. The second 3 digits indicate the tube chemical type,
and the last two digits number indicate the approximate range of the
tube. The higher the number, the higher the range.
4. Sampling Volume and Time. Using the standard number of pump
strokes, the concentration of the gas is read from stain length directly
matched to the printed scale after the listed sampling time has elapsed.
However, the range of the tube may be extended by using a smaller
or larger sample volume. In such cases, the scale reading must be
multiplied by a Correction Factor (CF) to adjust for the different sample
size. For example, the RAE Systems 10-103-18 hydrogen sulde tube
has a standard range of 25-250 ppm. When used with the standard
one stroke, the readings will correspond directly to the printed scale
on the tube. When used with half a stroke, a Ccorrection Factor (CF)
of 2 is applied. An observed reading of 50 ppm then corresponds to
an actual concentration of:
50 x 2 = 100 ppm
S No. 10-103-18
2
Standard
Range
25 - 250
210.5
20010050
2 x 111
0.512
Extended
Range
50 - 500
OPER ATION
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5. Cross-sensitivity. Gas detection tubes are generally quite selective,
but some compounds may interfere in the measurements. The Data
Sheet lists possible interfering compounds; others may also exist. In
most cases these compounds increase the stain length, but in some
cases they decrease the stain length. The user must be aware of
potential interferences, or incorrect readings may result.
2. In cases where a pre-tube is provided (e.g., Benzene 10-101-01 and
NOx 10-109-20), connect the pre-tube to the measurement tube using
the rubber connector in the direction indicated on the tube.
3.2.2 Testing Hand Pump For Leaks
Before a series of measurements, the pump used must be tested for leaks.
Follow this procedure:
1. Insert an unopened tube snugly into the inlet of the aspirating pump.
2. Align the red dot on the plunger with the red dot on the pump shaft.
3. Pull the plunger one full stroke and wait 2 minutes.
4. Rotate the plunger dot away from the pump shaft alignment mark,
and allow the plunger to be drawn back into the pump shaft. Keep
your hand on the shaft to keep it from snapping back too suddenly.
There are no leaks if the plunger returns to within 3 mm of its original
position. If a leak is detected, refer to Section 3.3 for maintenance
procedures.
3.2.3 Measurement Procedure
1.
Break both ends of a new detection tube using the tip breaker on the
side of the pump. Insert the tube until it stops, and then back off about 1
mm before breaking off the tip. The latter procedure allows the tip to fall
OPER ATION
into the tip reservoir at the end of the pump shaft. The reservoir can be
emptied by opening the rubber cover on the opposite side of the pump.
3. Insert the measurement tube securely into the rubber pump inlet. Point
the tube arrow towards the pump (see Figs. 3-1 and 3-2).
Insert open tube with arrow pointing towards pump.
4. Select the sample volume desired and align the red dot on the plunger
with the red dot on the pump shaft. Pull the handle quickly until it
latches at ½ or 1 full stroke (50 or 100 mL) and wait for the sampling
time indicated on the data sheet to allow the air to be drawn through
the tube. The end-of-ow indicator is dark during sampling. Flow is
complete when the end-of-ow indicator returns to its white color.
Withdraw plunger sharply until it locks in place, and rotate stroke counter.
Wait for indicated sampling time when end-of-ow indicator turns white.
OPER ATION
Break tube open at both ends.
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End-of-ow indicator is dark when sampling (left) and white when
sampling is complete (right).
5. For additional pump strokes, rotate the handle ¼ turn clockwise or
counterclockwise and push it back fully without removing the tube from
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3.2.4 Reading Tubes
1. The concentration of the compound being measured is read directly
from the scale printed on the tube.
the pump. Then repeat Step 4.
If additional strokes are needed, rotate plunger 90 degrees.
Push plunger back into pump shaft without removing tube.
Withdraw plunger for second stroke and repeat strokes as necessary.
Remove and read tube; return plunger and stroke counter to original position;
empty tube tip reservoir as necessary.
OPER ATION
2. The reading is taken as the furthest distance along the tube that the
color change just becomes visible. If the leading edge is diagonal
instead of perpendicular to the axis of the tube, use the average of the
minimum and maximum values. The three tubes shown in Figure 3-4
are all read as 0.9.
Figure 3-4. Reading of various types of endpoints after sampling.
3. Read the tube immediately after gas sampling, as colors may change,
fade, or disperse with time.
4. If a non-standard number of pump strokes was used for sampling,
multiply the reading by the Correction Factor given on the tube Data
Sheet (Chapter 5).
5. If humidity and temperature corrections are necessary as indicated on
the Data Sheets, multiply the observed readings by the given Correction
Factor(s) (CF) to obtain the true concentration. For more details and a
theoretical discussion, see Chapter 4.3 on the effects of humidity and
temperature.
OPER ATION
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6. The user must be aware of potential interfering compounds in the tube
measurements. Interferences can be either positive or negative.
CAUTION: Always examine the data sheet and other
available information for possible interferences. Failure to
consider interferences may lead to dangerously inaccurate
readings.
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3.3 Maintenance of the LP-1200 Piston Hand Pump
Replace the outlet check valve gasket if there is resistance on the
return stroke. Using the special tool or needle-nose pliers, unscrew
the plunger tip from the plunger rod. Replace the O-ring, check valve
gasket as necessary, and reassemble. Inspect the gasket ring in the
inlet end tting. If it is damaged, replace before screwing the end tting
back on.
Figure 3-5. Transparent view of LP-1200 pump
1. Tube Tip Reservoir
Remove the tube tip reservoir cover as needed to empty the broken
glass reservoir that is in the pump end tting.
2. Pump Inlet and Filter
The rubber pump inlet can become worn with use and result in leaks.
Unscrew the pump inlet nut and replace the rubber inlet. If the inlet
is not replaced, inspect the inlet lter and replace or clean the lter
when it becomes visibly dirty or if the end-of-ow indicator on the pump
shows that the ow takes longer than recommended on the tube box.
3. Pump Mechanism
The plunger gasket may leak if it is worn or not well lubricated. To
replace the gasket:
1. Unscrew the pump end tting on the handle side.
2. Pull the plunger out of the pump shaft.
3. Replace the gasket.
4. Carefully push the plunger back into the shaft. Use a ne
OPER ATION
screwdriver or tweezers to help ease the gasket into the shaft.
5. Lubricate the inside of the shaft with vacuum grease to ensure
a good seal.
showing internal parts.
3.4 Selection Of Sampling Pump
RAE Systems tubes are designed for operation with a RAE Systems hand
pump for drawing samples through RAE Systems tubes. Pumps from
different manufacturers may have different ow patterns or deliver different
volumes, which can cause signicant errors. For example, bellows hand
pumps as supplied by MSA and Draeger have substantially different ow
patterns.
Caution: Use of a sampling pump other than a RAE Systems
hand pump may cause serious errors. Always test any pump
for leaks before use.
3.5 Operation And Maintenance Of Remote Sampler
The Detection Tube Remote Sampler is designed for use with RAE Systems
hand pumps for gas-detection tubes and adsorption tubes. The exible
Remote Sampler allows gases to be sampled through narrow apertures,
down holes, or from other areas remotely located from the sampling pump.
The sampler is available in two lengths, 15 feet (4.5 meters), p/n 010-3009015, and 35 feet (11 meters), p/n 010-3009-035.
1. Installation
OPER ATION
Caution: Do not overtighten the plunger gasket. It could cause
a sudden loss of vacuum.
The inlet check valve may cause leaks if worn or not lubricated.
Unscrew the end tting on the inlet side and pull out the disk-shaped
rubber-inlet check valve. Replace as necessary, adding a light coat of
grease around the hole.
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Refer to Figure 3.7 for installation and part descriptions. Unscrew
the pump adapter nut and remove the standard rubber tube adapter
from the pump. Inspect the remote sampler to ensure that the porous
metal lter is in place, and screw the pump adapter nut attached to the
sampler into the pump. Store the standard nut and rubber adapter in a
safe place for later use.
2. Operation
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To ensure a good seal, insert the gas detection tube into the tube
holder and twist the tube while pushing in. If the tube uses a pre-tube,
insert the pre-tube into the pre-tube holder and push the pre-tube into
the end of the standard tube holder. Secure the pre-tube holder using
the rubber buckles. Lower the extension hose to the desired position.
Figure 3-6. Installation of the remote sampling probe into
the LP-1200 hand pump.
4. Routine Maintenance
a. Porous Metal Filter: The metal frit lter should be replaced when it
becomes visibly dirty or if the end-of-ow indicator on the pump shows
that the ow takes longer than recommended on the tube box.
b. Leak Test: If a leak is discovered with either pump, rst remove the
probe and check the pump for leaks. Then examine the tubing and
connections for the leak source, as follows:
i. Hand Pump: Insert a sealed tube into the tube holder tightly. Pull
3 pump strokes to expel the air from inside the tubing. Pull a
fourth stroke and wait for 2 minutes. Rotate the plunger dot away
from the pump shaft alignment mark, and allow for the plunger
to be drawn back into the pump shaft. Keep your hand on the
shaft to prevent it from springing back too suddenly. If the plunger
returns to within 3 mm of its original position, there are no leaks.
3. Correction
Caution: In order to obtain accurate readings, the following
corrective procedures must be employed when using the 35-foot
(11-meter) remote sampler.
OPER ATION
The 35-foot (11-meter) remote sampler causes a slight delay and
reduced reading because of the extra volume in the extension
tubing. Increase the sample time by 30 seconds for a 2-minute
tube, 20 seconds for a 1.5-minute tube, and by 15 seconds
for a 1-minute tube. Then multiply the reading by 1.08 to obtain the
corrected value. Corrections for the 15-foot (4.5-meter) remote sampler
are unnecessary.
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OPER ATION
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4. TECHNICAL INFORMATION
4.1 Gas Detection Tube Theory Of Operation
Gas detection tubes operate on a chemical reaction between the vaporphase compound and a liquid or solid detecting reagent, which is supported
on an inert matrix. The most common types of reactions are the following:
• Acid-base reactions These include reactions of acidic gases like HCl
and HF with bases, and reaction of alkaline vapors such as ammonia
with an acid in the tube. A dye present in the tube changes color as
the pH changes on exposure to the vapors.
• Reduction-oxidation (Red-ox) reactions These generate an oxidized
or reduced compound, which has a different color. The chlorine tube
uses oxidative coupling of colorless o-toluidine to form an orange azodye. White di-iodine pentoxide is reduced by CO and many organic
vapors to form deep brown-colored iodine. Orange chromium (VI) is
reduced by many organic compounds to form brown or green-colored
Cr(III) compounds.
• Ligand-exchange reactions These generate new complexes that
are more colored than the starting reagents. The most notable is the
conversion of white lead acetate to brown-black lead sulde in the
detection of H
the chlorine ligand of HgCl2 releases HCl, which then causes a pHdependent dye-color change.
S. In the case of phosphine, the exchange of PH3 for
2
TECHNICAL INFORMATION
•
Pre-layers or Pre-tubes These are used to condition the sample
by controlling humidity, removing interferences, or transforming the
analyte to another detectable compound. Examples include drying
OPER ATION
18
agents in NH3 and HCl tubes, organic removal by charcoal or oxidation
in selective CO tubes, and oxidation of NO to NO2 in the nitrogen oxides
tube.
All RAE Systems detection tubes are length-of-stain types. In these
tubes, the reaction of the gas with the supported reagent is fast, compared
to the transport of the bulk air sample through the tube. Therefore, all
of the detected vapors are reacted within the tube. As a result, there is
not a strong dependence of the readings on the rate at which the gas is
sampled. However, a very high ow rate can cause some smearing to a
high reading. Conversely, low ow rates are less likely to affect the stain
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length, but can give low readings by concentrating the colored products in
a shorter section of the tube. In cases of ow extremes, errors outside the
standard 25% accuracy can be produced.
RAE Systems tubes are calibrated using RAE Systems piston hand pumps.
The ow during a single pump stroke initially rises sharply and then decays
exponentially (see Figure 4-1). The best accuracy is therefore obtained
when the ow through the tube mimics this prole.
TECHNICAL INFORMATION
3. Precision. This value is determined by measuring a standard gas
sample with at least 5 randomly chosen tubes. Precision is reported
as the standard deviation from the average of the 5 measurements.
Precision is typically ≤±15%. (See Section 2 for complete table.)
4. Linearity with number of pump strokes. Multiple strokes are measured
with a gas standard with concentration at the low end of the tube.
Tubes must have correlation coefcients (r2) >0.95 to be considered
linear.
5.
Humidity. The effect on the reading as a function of humidity of the
standard gas is listed. Any required Correction Factors are tabulated.
6. Temperature. The effect of temperature is determined by equilibrating
the gas sample, tube, and pump to the test temperatures, typically 0°,
10°, 25°, and 40°C (32°, 50°, 77°, and 104°F). Any required Correction
Factors are tabulated. If humidity has a measurable effect on the gas
readings, the temperature tests are performed at constant relative
humidity (not absolute humidity). Any temperature corrections should
be multiplied by any humidity corrections to obtain true readings.
TECHNICAL INFORMATION
Figure 4-1. Piston pump internal pressure pattern. Data is offset
by 2 seconds.
4.2 Explanation Of Data Sheets
The Data Sheets supplied with each box of tubes give representative
information applying to all batches. The Data Sheets include:
1. Standard and extended measurement ranges, pump strokes
required, gas volumes required, sampling times, and the detection
limit. The standard range and strokes apply to the calibration scale
printed on the tubes. The range can usually be extended to higher
or lower concentrations by reducing or increasing, respectively, the
number of pump strokes.
2. Correction Factors (CF) for conditions of pump stroke, temperature,
humidity, or gas type other than the standard conditions. The
CF is multiplied by the observed reading to obtain the corrected
concentration.
20
7. Storage Life. Samples of tubes are stored for extended periods to
evaluate their accuracy at dened time periods to determine their
storage life. The user should store tubes in darkness at 3° to 7°C (37°
to 45°F) to maximize their shelf life. Freezing tubes (storage below
0°C, or 32°F) can damage some types and is not recommended.
8. Cross-Sensitivity. Tubes are challenged with a variety of possible
interfering gases to quantitate their relative response. Although the
tubes are highly selective, compounds that are chemically similar to
a target compound sometimes show a positive interference. Others
interfere with the measurement gas without showing a response
on their own; for example, when acidic vapors coexist with basic
vapors. Such information is listed in a separate note or column titled
“Interferes in Mixtures.” The user should know as much about the
sample environment as possible in order to make sound judgments
regarding possible interferences; otherwise inaccurate readings may
result. In some cases, a different color or pattern of the stain can clue
the user to the presence of an interfering compound.
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4.3 Humidity, Temperature, Pressure, and Matrix Effects
2. Temperature
1. Humidity
Humidity has little effect on most tubes either because the reaction is
insensitive to moisture or because drying agents are added to absorb
the moisture in a pre-layer (see Figure 4-2). Humidity tends to have
the greatest effect on compounds that are highly water-soluble, such
as acids and bases. HF (hydrouoric acid) is a notable example that
requires humidity corrections; water-adsorbing prelayers cannot be
used because they tend to be reactive with HF. The humidity effect
tends to be greater as the concentration range of the tube is lowered.
When correcting for humidity, the CF is multiplied by the reading in
addition to multiplying by any temperature correction. Any necessary
TECHNICAL INFORMATION
Correction Factors are listed in the individual tube data sheets. Note
that the relative humidity at the measurement temperature denes the
correction, rather than the absolute humidity.
Temperature can affect gas tube readings in at least three ways. First,
as the temperature increases, the gas density decreases, causing a
tendency for the reading to decrease (see pressure effects described in
the next section). Second, as the temperature increases, the reaction
rate increases, causing the reading to be sharper and shorter. A third,
balancing effect is that adsorption is often a prerequisite for reaction.
Adsorption is weaker as temperature increases, and thus the reading
can become longer. The interplay of these competing effects results in
some stains that are longer with increasing temperature, and others
that are shorter.
TECHNICAL INFORMATION
Figure 4-2. Effect of humidity on gas detection tube readings.
22
Figure 4-3. Effect of temperature on gas detection tube readings.
Additional factors occur in special cases. For example, pretube or prelayer
reactions are sometimes more complete at higher temperatures,
causing higher readings in the measurement layer.In some cases,
the color of the stain can change. In the water vapor 120-20 tube, the
color stain is green at room temperature and a more purple color below
room temperature.
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3. Pressure
Tubes change color in proportion to the mass of the compounds
reaching the reagent (i.e, the absolute concentration). Therefore, as
the pressure decreases at higher altitudes, the apparent response is
reduced because there are fewer molecules per unit volume sampled.
The conventional desired reading is in ppmv (parts per million by
volume), which is a relative concentration, such as a mole or volume
fraction (% of molecules of compound per molecules of total gas [air]),
rather than an absolute concentration.
All RAE Systems tubes are calibrated at 1 atmosphere (760 mm
Hg) pressure at sea level.
• For tubes calibrated in absolute concentrations such as lbs./MMCF or
TECHNICAL INFORMATION
mg/m3, no pressure corrections are needed.
Example LocationAltitude
(km)
Altitude
(feet)
Pressure,
(mm Hg)
San Francisco, CA007601.00
Atlanta, GA0.310007311.04
Spokane, WA0.620007031.08
Rapid City, SD0.930006761.12
Salt Lake City, UT1.240006501.17
Denver, CO1.550006251.22
Colo. Spgs., CO1.860006011.27
Santa Fe, NM2.170005781.32
Alta, UT2.480005551.37
Winter Park, CO2.790005341.42
Keystone, CO3.0100005141.48
4. Matrix Gas
CF
TECHNICAL INFORMATION
• For tubes calibrated in relative concentrations (e.g., ppm), correct for
pressure using one of the following equations:
Corrected reading = Observed Reading x 760 mm Hg
Pressure (mm Hg)
Corrected reading = Observed Reading x 101.3 kPa
Pressure (kPa)
Corrected reading = Observed Reading x 14.7 psia
Pressure (psia)
The pressure in mm Hg can be estimated as a function of altitude using
the following equation:
P (mm Hg) = 760exp(-0.1286[alt(km)]) below 2 km
Example Correction Factors are listed in the following table as a
function of altitude. Weather changes may also affect the atmospheric
pressure, but the necessary corrections are usually <10%.
The matrix gas usually has little or no effect on the tube readings
as long as the gas does not chemically react with the tube reagents
or measured compound. Thus, readings in air, nitrogen, hydrogen,
helium, or carbon dioxide give essentially the same results. However,
the viscosity of the gas has a signicant effect on the sampling time.
Thus, for example, the sampling time of the CO 10-102-18 tube is
about half as long in pure hydrogen (viscosity 9.0 μPa-s) as it is in air
(viscosity 18.6 μPa-s).
*Data based on RAE pumps and tubes used in standard range.
** The entire tube changes to very light pink, no boundary.
=CHCH=CH2 + KMnO2 → Oxidation products
2
Concentration
(ppmv)
750000
40000
50.5
100.5
500
Apparent
Reading*
Caution: Dispose of spent or expired tubes according to local regulations.
Possibly hazardous materials are given under the section Reaction Principle.
Data SheetS
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Page 20
Benzene C
No. 10-101-20
6H6
n-Butane n-C4H10 No. 10-137-30
Extended
Range
Range (ppmv)2.5 - 50
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
* Data based on RAE Systems pumps and tubes used in standard range.
**Very light blue.
**
Other Possible Interferences: Other hydrocarbons; most organic vapor interferences
are eliminated by the pretreatment layer. An additional charcoal lter tube (p/n 025-
2000-010) can be used to further reduce cross-sensitivity by organic vapors. Can
be used to measure CO in pure hydrogen.
Data SheetS
42
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Carbon Monoxide CO No. 10-102-20
Carbon Monoxide CO No. 10-102-30
Extended
Range
Range (ppmv)2.5 - 50
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
210.5
20010050
2 x 221.5
0.512
Standard
Range
5 - 100
Extended
Precision (Relative Standard Deviation)*: ≤±12%
2
Linearity with No. of Pump Strokes: r
>0.99
Humidity: No effect 5 - 100% RH.
Temperature Range: 0 - 40°C (32 - 104°F)
Temp (°C/°F)0/3210/5025/7740/104
Corr. Factor0.800.831.01.15
Storage Life: 2 years in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: White → Light Brown Ring
Reaction Principle: 5CO + I
Data SheetS
Cross-sensitivity:
Substance
NO
H
S
2
NH
3
CH
4
Hexane
Isobutylene
Toluene
Trichloroethylene
* Data based on RAE Systems pumps and tubes used in standard range.
+ H2S2O7 → I2 + CO2 + sulfur products
2O5
Concentration
(ppmv)
Apparent
Reading*
2000
1000
3000
250000
1000
1000
1000
2520 (v faint)
Other Possible Interferences: Most hydrocarbon interferences are eliminated in
the pretreatment layer. Can be used to measure CO in pure hydrogen.
Range
10 - 200
Extended
Range
Range (ppmv)10-250
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
210.5
20010050
2 x 221.5
0.512
Standard
Range
20 - 500
Extended
Range
40 - 1000
Precision (Relative Standard Deviation)*: ≤±15%
Linearity with No. of Pump Strokes: r
2
= 0.999
Humidity: No effect 5 - 95% RH.
Temperature Range: No effect 0 - 40°C (32 - 104°F)
Storage Life: 2 years in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: White → Light Brown
Reaction Principle: Prelayer removes most interferences
5CO + I
Cross-sensitivity:
Substance
+ H2S2O7 → I2 + CO2 + sulfur products
2O5
Concentration
(ppmv)
Apparent
Reading*
NO2000
H
S
2
NH
3
CH
4
Hexane
Hexane
Isobutylene
Toluene
Trichloroethylene
* Data based on RAE Systems pumps and tubes used in standard range.
** Very light green.
1000
3000
250000
1000
40018
1000
1000
2515**
Other Possible Interferences: Hydrocarbons and similar reducing gases. Most
organic vapor interferences are eliminated by the pretreatment layer and can
be further removed using a pretreatment tube such as p/n 025-2000-010 VOC
zeroing tube. Methane does not interfere in mixtures.
Data SheetS
44
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Carbon Monoxide CO No. 10-102-45
Chlorine Cl2 No. 10-106-10
Extended
Range
Standard
Range
Extended
Range 0.1 - 2%0.2 - 4%0.4 - 8%
No. of Pump Strokes210.5
Sample Volume (mL)20010050
Sample Time (min)2 x 1.51.51
Correction Factor0.512.0
Precision (Relative Standard Deviation)*: ≤±10%
2
Linearity with No. of Pump Strokes: r
= 0.999
Humidity: No effect 5 - 100% RH.
Temperature Range: No effect 0 - 40°C (32 - 104°F)
Storage Life: 2 years in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: White → Dark Brown
Reaction Principle: 5CO + I
Cross-sensitivity:
Substance
H
S1000
NH
CH
2
3
4
Data SheetS
+ H2S2O7 → I2 + CO2 + sulfur products
2O5
Concentration
(ppmv)
Apparent
Reading*
3000
250000
Hexane6000.4%
Hexane12001.2%
Isobutylene1000
Toluene1000
* Data based on RAE Systems pumps and tubes used in standard range.
Other Possible Interferences: Hydrocarbons and similar reducing gases. An
additional charcoal lter tube (p/n 025-2000-010) can be used to reduce cross-
sensitivity by organic vapors. Methane does not interfere in mixtures.
Range
Extended
Range
Range (ppmv)0.25 - 4
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
210.5
20010050
2 x 2.52.52
0.512
Standard
Range
0.5 - 8
Extended
Range
1.0 - 16
Precision (Relative Standard Deviation)*: ≤±20%
Linearity with No. of Pump Strokes: r
2
= 0.99
Humidity: No data
Temperature Range: 0 - 40°C (32 - 104°F)
Temp (°C/°F)0/3210/5018/7040/104
Corr. FactorNDND1.0ND
Storage Life: 1 year in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: White → Yellow
Reaction Principle: Cl
Cross-sensitivity:
Substance
ClO
2
CO
2
NH
3
NO
2
CH
4
S
H
2
Isobutylene
*
Data based on RAE Systems pumps and tubes used in standard range.
#
Interferes in mixtures
+ o-Tolidine → Yellow colored product + HCl
2
Concentration
(ppmv)
Apparent
Reading*
12
150000
500000
#
57
250000
2500
20000
.
Other Possible Interferences: Other oxidizing gases.
Data SheetS
46
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Chlorine Cl2 No. 10-106-20
Chlorine Dioxide ClO2 No. 10-130-10
Extended
Range
Range (ppmv)0.25 - 50
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
210.5
20010050
2 x 221.5
0.512
Standard
Range
5 - 100
Extended
Precision (Relative Standard Deviation)*: ≤±20%
2
Linearity with No. of Pump Strokes: r
= 0.999
Humidity: No effect 0-90% RH
Temperature Range: No effect between 0 - 40°C (32 - 104°F)
Storage Life: 1 year in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: White → Orange
Reaction Principle: Cl
Cross-sensitivity:
Substance
ClO
Data SheetS
2
CO
CO
2
NO
NH
3
CH
4
S
H
2
SO
2
Hexane
Isobutylene
Toluene
Data based on RAE Systems pumps and tubes used in standard range.
*
+ o-Tolidine → Orange colored product + HCl
2
Concentration
(ppmv)
Apparent
Reading*
109
2500
500000
1005
1000
250000
100
20000
1000
1000
1000
Range
10 - 200
Extended
Range
Standard
Range
Extended
Range
Range (ppmv)0.05 - 20.25 - 150.5-30
No. of Pump Strokes510.5
Sample Volume (mL)50010050
Sample Time (min)5 x 221
Correction Factor0.1912.1
Precision (Relative Standard Deviation)*: ≤±20%
Humidity: No effect 10-90% RH
Temperature Range: No effect 0 - 40°C (32 - 104°F)
Storage Life: 1 year in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: White → Yellow
Reaction Principle: ClO
Cross-sensitivity:
Substance
Cl
2
+ o-Tolidine → Yellow colored product
2
Concentration
(ppmv)
Apparent
Reading*
106
NO252
NO
NH
CH
2
3
4
511
500000
100000
HCl10000
H2S20000
CO5000
CO
2
150000
Isobutylene20000
* Data based on RAE Systems pumps and tubes used in standard range.
Other Possible Interferences: Bromine
Data SheetS
Other Possible Interferences: Other oxidizing gases.
48
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Diesel & Jet Fuel No. 10-143-10
Diesel & Jet Fuel (continued)No. 10-143-10
Range (ppmv)
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
Extended
Range
Do not extend
Standard
Range
0.5 - 25
4
400
4 x 1.5
1
Extended
Do not extend
Precision (Relative Standard Deviation)*: ≤±20% for undecane
* Data based on RAE Systems pumps and tubes used in standard range.
Other Possible Interferences: No response to 3000 ppm CO, 300 ppm NH3, or 200 ppm SO2.
Range
Extended
Range
Range (ppmv)0.5 - 10
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
210.5
20010050
2 x 110.5
0.512
Standard
Range
1 - 20
Extended
Range
2 - 40
Precision (Relative Standard Deviation)*: ≤±20%
2
Linearity with No. of Pump Strokes: r
= 0.999
Humidity: Must be used @ <5% RH. Reading drops sharply above 5% RH.
Temperature Range: No effect between 0 - 40°C (32 - 104°F) at <5%RH.
Storage Life: 2 year in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: Yellow → Pink
Reaction Principle: HCl + Base → Chloride Salt + H
Cross-sensitivity:
Substance
CO
CO
2
S
H
2
SO
2
NO
NO
2
NH
3
HF
Cl
2
CH
4
Hexane
Toluene
* Data based on RAE Systems pumps and tubes used in standard range.
Other Possible Interferences: Other acid vapors; amines and other bases.
Concentration
(ppmv)
15,0000
8,0000
8000
2000
1000
20020
1000
2515
100
25,0000
24000
4000
Apparent
Reading*
O (dye color change)
2
Data SheetS
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Hydrogen Chloride HClNo.10-108-10
Hydrogen Chloride HCl No. 10-108-22
Extended
Range
Range (ppmv)0.5 - 10
Standard
Range
1 - 20
No. of Pump Strokes210.5
Sample Volume (mL)20010050
Sample Time (min)2 x 110.5
Correction Factor0.512
Precision (Relative Standard Deviation)*: ≤±20%
Linearity with No. of Pump Strokes: r
2
= 0.999
Humidity: Calibrated at 50% RH and 23 °C (73 °F).
% Relative Humidity< 5%30%50%70%90%
Correction Factor @ 10 ppmv0.70.81.01.12.7
Temperature Range: No effect between 0 - 40°C (32 - 104°F) at <5% RH.
Storage Life: 2 years in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: Yellow → Pink
Reaction Principle: Pretube reduces humidity
Data SheetS
Cross-sensitivity:
Substance
HCl + NaOH → NaCl + H
Concentration
(ppmv)
Apparent
Reading*
O (dye color change)
2
CO15,0000
CO
2
8,0000
H2S8000
SO
2
2000
NO1000
NO
NH
2
3
20020
1000^
HF2515
Cl
CH
2
4
10>20
25,0000
Hexane24000
Toluene4000
* Data based on RAE Systems pumps and tubes used in standard range.
^Interferes in mixtures
Other Possible Interferences: Other acid vapors; amines and other bases.
Extended
Range
2 - 40
Extended
Range
Range (ppmv)10-250
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
210.5
20010050
2 x 1.51.51.0
0.512.0
Standard
Range
20-500
Extended
Range
40-1000
Precision (Relative Standard Deviation)*: ≤±20%
2
Linearity with No. of Pump Strokes: r
> 0.995
Humidity: No effect 5-95% RH.
Temperature Range: No effect 0 - 40°C (32 - 104°F); at -20°C, the response
is reduced by about 5%.
Storage Life: 2 years in darkness at 5 °C (40°F). Refrigeration required.
Color Change: Yellow → Red
Reaction Principle: HCl + Base
Cross-sensitivity:
Substance
CH
4
CO
CO
2
S
H
2
SO
2
NO
NO
2
NH
3
HF
Cl
2
Hexane
Toluene
* Data based on RAE Systems pumps and tubes used in standard range.
→ Chloride (dye color change)
Concentration
(ppmv)
Apparent
Reading*
250000
5000
10000
1000
10000
2000
1000
1000
1000
2000
20000
20000
Data SheetS
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Hydrogen Cyanide HCN No. 10-126-10
Hydrogen Fluoride HF No. 10-105-10
Extended
Range
Range (ppmv)1.25 - 30
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
421
400200100
4 x 2.52 x 2.52.5
0.412
Standard
Range
2.5 - 60
Extended
Precision (Relative Standard Deviation)*: ≤±20%
Linearity with No. of Pump Strokes: r2 >0.999
Humidity: 5% - 95%RH
% Relative Humidity< 5%10%50%95%
Correction Factor @ 10 ppmv1.01.01.21.4
Temperature Range: No effect 0 - 40°C (32 - 104°F)
Storage Life: 1 year in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: Yellow → Red (ignore light orange color formed in clean air)
Reaction Principle: 2HCN + HgCl
→ Hg(CN)2 + 2HCl
2
HCl + Base → Chloride Salt + H2O (dye color change)
Data SheetS
Cross-sensitivity:
Substance
H
2
CH
4
CO
S
H
2
HCl
SO
2
NH
3
CO
2
* Data based on RAE Systems pumps and tubes used in standard range.
#
Measured in dry gas; at >20% RH, no response is observed by these gases.
Concentration
(ppmv)
20000
250000
3000
100<1
100<1
2020
500
50000
Apparent
Reading*
#
#
#
Note: A light orange color may form when drawing in air with no HCN present. This
color can be ignored and does not affect true HCN readings, which form a bright
pinkish-red color. The color boundary is sharp in ambient, humid air and somewhat
diffuse in very dry air.
Range
5 - 120
Extended
Range
Range (ppmv)0.25 - 10
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
842
800400200
8 x 0.54 x 0.52 x 0.5
0.411.6
Standard
Range
0.5 - 20
Extended
Range
1 - 40
Precision (Relative Standard Deviation)*: ≤±20%
Linearity with No. of Pump Strokes: r
2
= 0.98
Humidity: Calibrated at 50% RH and 23°C (73°F).
% Relative Humidity30%40%50%60%70%80%90%
Correction Factor0.30.41.01.31.62.02.6
Temperature Range: No effect 10 - 30°C (50 - 86°F) at constant 41% RH.
Storage Life: 2 years in darkness at 5 - 25°C (40 - 77°F). Refrigeration Preferred.
Color Change: Beige → Purple
Reaction Principle: HF + NaOH → NaF + H
Cross-sensitivity:
Substance
Concentration
(ppmv)
O
2
Apparent
Reading*
CO2500
CO
2
NH
3
NO
S
H
2
SO
2
CH
4
HCl
Cl
2
* Data based on RAE Systems pumps and tubes used in standard range.
#
Pink color over entire tube length.
^ May interfere in mixtures.
500000
3000^
1000
8000
2000
250000
4entire tube
15entire tube
#
#
Other Possible Interferences: Other acid vapors; amines and other bases. No
effect of 100 ppm toluene or 2400 ppm hexane.
Data SheetS
60
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Hydrogen Sulde H
S No. 10-103-04
2
Hydrogen Sulde H
S No. 10-103-05
2
Extended
Range
Range (ppmv)0.1 - 1.5
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
210.5
20010050
2 x 1.51.51
0.512
Standard
Range
0.2 - 3
Precision (Relative Standard Deviation)*: ≤±12%
2
Linearity with No. of Pump Strokes: r
= 0.999
Humidity: Tubes must be used @ <5% RH. Reading drops sharply above 5% RH.
Temperature Range: No effect between 0 - 40°C (32 - 104°F).
Storage Life: 1 year in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
* Data based on RAE Systems pumps and tubes used in standard range.
‡ Forms light green stain when methanol is above 70 ppm. Water can be measured in
a mixture with methanol by reading the dark green stain only, ignoring the light green
methanol stain beyond dark green end point. See Technical Note 179 (rev 1 wh 11-04) for
pictures.
Other Possible Interferences: Amines, alcohols. No response to heptanes,
octanes as present in “rich” natural gas or commonly called “condensate.”
Extended
Range
4 - 20
1.5 min
45 sec
Extended
Range
Range (lbs/MMCF)3 - 20
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
* Data based on RAE Systems pumps and tubes used in standard range.
# No interference in mixtures with water vapor. ‡ No response below 80 ppm. Light green
stain when methanol is above 80 ppm, 340 ppm alone reads ~30 lbs/MMCF. Water can be
measured in a mixture with methanol by reading the dark green stain only, ignoring the light
green methanol stain beyond the dark green end point.
**Note: Color tends towards purple as temperature decreases.
Other Possible Interferences: Amines, alcohols; no effect of 500 ppm PH
.
3
Data SheetS
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TN-179 Technical Note
Effect of Methanol & Glycols on Water Vapor Tubes
On the 120-20 (6-40 lbs/MMCF) tubes, the water forms a purple stain followed by a
light green stain for methanol (see Figure 2). This light green color can be ignored
and only the darker stain read to obtain the water vapor concentration.
Introduction
Colorimetric tubes for water vapor are commonly used to measure the humidity of
natural gas because of their rapid response compared to instrumental methods.
To minimize corrosion and to obtain a better selling price for the gas, water vapor
levels are often reduced by passing the gas through a liquid scrubber containing
ethylene glycol or triethylene glycol. In addition, methanol is sometimes added to
the natural gas pipeline as an antifreeze so that ice does not accumulate during
cold weather. This technical note describes how to read water vapor tubes that
may have interference from these chemicals.
Resistance to Glycol Response and “Rich” Gas
Newer versions of RAE Systems water vapor tubes have been improved to
remove any response to ethylene glycol or triethylene glycol. These changes were
implemented in the 6-40 lbs/MMCF tubes (p/n 10-120-20) shipped after November
2003 and in the 2-10 lbs/MMCF tubes (p/n 10-120-10) shipped after November
2004. Higher alkanes such as pentane, hexanes and octanes present in "rich"
natural gas also cause no response.
Effect of Methanol
Methanol alone causes a light green response in both 120-10 and 120-20 tubes
when its concentration is above about 80 ppm. When water and methanol are
present together, a two-tone stain is seen. On the 120-10 (2-10 lbs/MMCF) tubes,
the water forms a medium-dark green stain followed by a light green stain for
methanol (see Figure 1).
Data SheetS
H2O: 0 Methanol: 60 ppm
H2O: 10 lbs/MMCF Methanol: 79 ppm
H2O: 20 lbs/MMCF Methanol: 158 ppm
O: 30 lbs/MMCF Methanol: 237 ppm
H
2
H
O: 40 lbs/MMCF Methanol: 316 ppm
2
Figure 2. Methanol response on 120-20 (6-40 lbs/MMCF) tube.
0°C/32°F H
O: 20 lbs/MMCF Methanol: 100 ppm
2
Data SheetS
H
O: 6 lbs/MMCF Methanol: 60 ppm
2
H
O: 0 Methanol: 100 ppm
2
H2O: 8 lbs/MMCF Methanol: 100 ppm
Figure 1. Methanol response on 120-10 (2-10 lbs/MMCF) tube.
96
20°C/68°F H
30°C/86°F H
O: 20 lbs/MMCF Methanol: 100 ppm
2
O: 20 lbs/MMCF Methanol: 100 ppm
2
Figure 3. Effect of Temperature on 120-20 tube.
Figure 3 shows that the color stain for water vapor is greener at higher temperatures
and tends towards purple as the temperature is lowered. Therefore the distinction
between methanol and water vapor response is clearer at lower temperatures.
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Water Vapor (Metric) H2O No. 10-120-30
Water Vapor (Metric) H2O No. 10-120-40
Extended
Range
Range (mg/L)0.025 - 0.5
No. of Pump Strokes
Sample Volume (mL)
Sample Time (min)
Correction Factor
Storage Life: 2 years in darkness at 5 - 25°C (40 - 77°F). Refrigeration preferred.
Color Change: White → Reddish Brown
Reaction Principle: C
Cross-sensitivity:
Substance
Data SheetS
p-Xylene100100
o-Xylene
m-Xylene
Toluene
Benzene
Hexane
Isobutylene
CO
CO
2
S
H
2
NO
NH
3
CH
4
SO
2
+ I2O5 + H2SO4 → I2 + oxidation products
8H10
Concentration
(ppmv)
10040 (brown)
10020 (brown)
2050 (brown)
1010 (v.faint)
1000
1000
2500
500000
50000
1003 (v.faint)
1000
250000
100
Apparent
Reading*
Data SheetS
*Data based on RAE Systems pumps and tubes used in standard range.
Note: The tube is calibrated to p-xylene.
Other Possible Interferences: Other aromatics.
100
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6. SPECIALTY TUBES
6.1 Smoke Generating Tubes
Smoke generating tubes are designed for use in respirator t tests. These
tubes are of the stannic chloride type required by OSHA for use in the
irritant smoke t test procedure. The tubes can also be used for visualizing
air currents, such as in testing the performance of fume hoods or in
detecting leaks from an air duct.
1. Operation
Smoke tubes are operated by simply breaking open each end and inserting
into a rubber squeeze bulb or other pump. Air pushed through the tube
releases the stannic chloride, which decomposes on contact with moisture
in the air to form a smoke. The tubes can be re-used until no more smoke
is evolved. Rubber caps are provided to seal the tubes between uses.
2. Smoke Tube Kit
The Smoke Tube Kit (Part no. 010-0004-000) contains the following:
• Aspirator bulb
• Tube tip breaker
• 1 Box of 6 smoke tubes
• Soft carrying case
Data SheetS
SPECIALTY TUBES
Figure 6.1. Use of smoke tube for visualizing fume hood air
currents.
102
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Gas Generation Tube Data Sheet
6.2 RAE-Sep™ Tube s
Irritant Smoke No. 10-123- 01
Color: A white smoke is generated. The tube changes from a dark reddish brown to a
lighter reddish brown. The tube can be used repeatedly until it is spent. Keep the tube
closed between uses with the supplied rubber caps.
Humidity Range: 10 - 95% RH. The smoke generating life increases about 10% at 20%
RH and decreases about 10% at 80% RH (incoming air humidity).
Temperature Range: 0 - 40°C (32 - 104°F). As temperature decreases the smoke lasts
longer and is less intense.
Storage Life and Conditi
CAUTIONS ON USE:
• Read, understand and comply with all labels, warnings and instructions accompanying
these tubes before use. Failure to comply may cause serious injury or death.
• For use in respirator t testing according to OSHA 29 CFR 1910.134 (appendix A) and
OSH A 19 10 .139 .
• Wear safety glasses and gloves to protect against chemical exposure and ying
glass. Wear a respirator when exposed to smoke. Vapors are corrosive to skin and
overexposure can result in serious injury or death.
• DO NOT inhale smoke directly. If inhaled enough to cause coughing, remove victim to
fresh air. If coughing persists, provide oxygen and contact a physician.
• Use only in a well-ventilated area. DO NOT use in a conned space.
• DO NOT use under a respirator t testing hood or other enclosed space because fume
concentrations may build up to levels that can cause serious injury or death.
• Avoid contact of smoke with skin. DO NOT direct smoke stream directly at the skin
dur ing t testing. If smoke contacts skin for prolo nged time, skin burns can result; ush
with copious amounts of water for 15 minutes and contact a physician.
• If smoke contacts eyes, immediately ush with water for 15 minutes and contact a
physician. Eyes should be kept tightly closed during t testing.
• Use only the pump(s) and ow rates specied in OSHA CFR 1910.134 and 29 CFR
1910.139. If the pump is operated at non-specied ow rates it could increase the
smoke and fume concentrations and cause serious injury or death.
• Do not use smo ke tubes in areas that may contac t food or food eat ing areas. Ingesti on
of tube contents or fodd exposed to smoke may cause serious injury or death.
• Do not use for t testing on persons with pre- existing respiratory or related medical
conditions or are allergic to tin compounds or hydrochloric acid.
• When using for visualizing air currents, avoid exposure to persons downstream of the air ow.
SPECIALTY TUBES
Disposal: Dispose of spent or expired tubes according to local regulations. Each tube
contains 1.0 g of stannic chloride before use. Tube contents generate hydrochloric acid on
contact with water.
ons: 2 years in darkness at 5 - 25°C (40 - 77°F)
RAE- Sep™ tubes are short separatio n tubes designed
for use with the UltraRAE 3000 Specic Compound
Monitor. The UltraRAE 3000 is a photoionization
detector (PID) that measures the concentration of
the target compound after a xed sampling time.
The tubes themselves are not calibrated, but rather
serve as lters before the PID to allow selective
measurements in dened applications. Current
applications include ben zene in gasoline vapors and
renery processes, butadiene in polymer and rubber
manufacturing, and halocarbons such as methylene
chloride in the presence of other organic solvents
in the petrochemical industry. RAE-Sep™ tubes
achieve their selectivity by a combination of chemical
absorption and physical adsorption of potentially
interfering compounds. Each RAE-Sep tube must be
used with its dedicated lamp in order to guarantee
accurate measurement.
Measurements are initiated by inserting an opened
tube and pushing the Start key. The unit then
samples for a pre-dened interval and displays the
result at the end. Each tube is intended for a single
use to avoid breakthrough of interfering compounds.
Figure 6.2.
UltraRAE 3000 Specic Compound Monitor.
SPECIALTY TUBES
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RAE-Sep™ Tube Data Sheet
RAE-Sep™ Tube Data Sheet
Benzene C
Standard LampTypical Range (ppmv)
9.8 eV0.1 - 1000
No. 012-3022-010
6H6
Temperature Range: 2 - 40°C (36 - 104°F)
Temp (°C)2-1010-1515-3030-40
Temp (°F)36-5050-6060-8686-104
Measure Time (sec)150906040
Sample Vol. (mL)900540360240
Calibration should be performed at the same temperature as the measurement.
It is preferable to recalibrate when changing batches.
Humidity: No effect on reading 0 - 95% RH. Humid, clean air drawn through the
tube before measurement will reduce VOC capacity. Caution: Drawing humid air
for extended periods or liquid water through the tubes may damage the instrument.
Storage Life and Conditions: Unopened tubes can be stored for 1 year in darkness
at 5 - 25°C (40 - 77°F). Refrigeration is preferred. Open tubes should be used
within one hour to avoid loss of capacity.
Color Change: Yellow → Brown → Green
The benzene reading may be high if the green color extends to more than ¾ of the
length. The tube may still have some capacity if there is no green color.
* Not necessarily the maximum allowable conc. ** No effect on tube capacity. Propane and
higher hydrocarbons do affect capacity. # Higher amounts may reduced benzene response.
Note: Each tube contains 3 mg of chromium compounds.
Test
Conc.
(ppmv)*
#
Apparent
Benzene
Response
0.0Isopropanol1000.0
Substance
Test
Conc.
(ppmv)*
#
#
Apparent
Benzene
Response
0.0
0.4
Butadiene(Polymer)
C4H6 No. 012-3024-010
Standard LampTypical Range (ppmv)
9.8 eV0.1 - 200
Temperature Range: 5 - 40°C (41 - 104°F)
Temp (°C)
Temp (°F)
5-1818-3030-40
41-6464-8686-104
Measure Time (sec)1807550
Sample Vol. (mL)1500600400
Calibration should be performed at the same temperature as the measurement.
Humidity: 0 - 95% RH.
RH<5%50%80%
Correction Factor (CF)1.01.51.6
When calibrated with dry gas, multiply the reading by the CF to obtain true value.
Color Change: None
Storage Life and Conditions: Unopened tubes can be stored for 2 years in
darkness at 0 - 40°C (32 - 104°F). Open tubes may be stored for up to 8 hours
* Not necessarily the maximum allowable concentration. ** Methane above 1% by volume
reduces the PID response, but has no effect on tube capacity. Butane and higher hydrocarbons
reduce capacity. # Methyl bromide can be measured using a 10.6 eV lamp and a 60 sec.
sampling time at
sampling time at 22°C. 1,2-DCA, TCA, TCE, and PCE do not interfere. 1,1-DCE gives about
a 30% cross-sensitivity. ‡ Ammonia can be measured using a 10.6 eV lamp and a 75 sec.
sampling time at 22°C. Adjust time at other temperatures proportionately.
Note 1: Unused tubes contain no hazardous components but may adsorb toxic
compounds from the environment.
Note 2: For more details on tube operation see Technical Note 147.
Test
Conc.
(ppmv)*
#
22°C
53
## Vinyl chloride can be measured using a 10.6 eV lamp and a 30 sec.
.
Apparent
Butadiene
Response
#
Substance
##
Trichloroethylene400
Test
Conc.
(ppmv)*
4017
Apparent
Butadiene
Response
##
SPECIALTY TUBES
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RAE-Sep™ Tube Data Sheet
Halocarbon (CH
Standard LampTypical Range (ppmv)
11.7 eV0.1 - 200
Temperature Range: 2-40°C (41-104°F)
Substance
Methyl Chloride30180Temp
Methylene Chloride
(MC)
Chloroform45260
Carbon Tetrachloride60350
Calibration should be performed at the same temperature as the measurement.
Humidity: No effect on reading 0 - 95% RH. Humid, clean air drawn through the
tube before measurement will reduce VOC capacity. Caution: Drawing humid air
for extended periods or liquid water through the tubes may damage the instrument.
Storage Life and Conditions: Unopened tubes can be stored for 1 year in darkness
at 5 - 25°C (40 - 77°F). Open tubes may be stored for up to 8 hours in clean air at
50% RH without signicant loss of capacity.
Color Change: Orange → Brown
Reading may be high if tube is discolored to more than ¾ of its length.
Storage Life and Conditions: Unopened tubes can be stored for 1 year in darkness
at 0 - 40°C (32 - 104°F). Open tubes may be stored for up to 8 hours in clean air
* Not necessarily the maximum allowable concentration.
** Methane above 1% by volume reduces the PID response, but has no effect on tube
capacity. Butane and higher hydrocarbons reduce tube capacity.
Note 1: Each tube contains about 3 mg of chromium compounds.
Note 2: For more details on tube operation see Technical Note 133.
Meas.
Time
(sec)
30180Time
Test Conc.
(ppmv)*
)No. 012-3023-010
2Cl2
Vol.
(mL)
Temp
(°C)
(°F)
(sec)
Apparent MC
2-1010-1515-3030-40
36-50 50-6060-8686-104
3x2x1x0.67x
Response
6.3 PID Conditioning Tubes
Three types of tubes, VOC Zeroing, VOC/CO2 Zeroing, and Humidity
Filtering, are designed primarily for use with photoionization detectors
(PIDs), but may have uses as pre-lters in other applications as well.
These tubes are not calibrated and show no color change. They have the
same 7 mm diameter as RAE-Sep™ tubes and require an adapter (p/n
025-3002-000) to connect to a PID or other instrument.
VOC Zeroing Tubes
VOC Zeroing tubes are single-use charcoal lters intended for zero
calibration, especially for the ppbRAE 3000, where a zero gas with <5 ppb
isobutylene-equivalent response is required. Other charcoal tubes with
higher capacity might also be used for this purpose, but once they have
been opened for some time, they tend to absorb VOCs from the ambient
air and then release ppb levels of VOCs back into the zero calibration
stream. The VOC Zeroing tubes ensure a clean background by virtue
of being sealed in glass until just before use. These tubes could also
be used to remove organic vapor interferences in other sensors such as
electrochemical CO sensors or unltered CO tubes.
VOC/CO2 Zeroing Tubes
These tubes are identical to the VOC Zeroing Tubes, but with an additional
layer to remove CO2 for multi-gas meters having both PID and CO2
sensors.
Humidity Filtering Tubes
The Humidity Filtering II tubes are designed to dry the sample gas stream
and thus avoid humidity effects on PID measurements. High humidity
reduces PID response by up to 50% with a properly maintained PID. If
the PID sensor is dirty, humidity over 80% can cause a current leakage
that appears as a drifting, irreproducible rise in readings. By reducing
the sample humidity to <20%, the Humidity Filtering II tubes remove both
effects. The tubes last for approximately 1/2 hour and can be reused
until spent. They are especially useful in soil remediation applications that
have high humidity, and common contaminants are non-polar compounds
such as gasoline and trichloroethylene. Losses of some compounds
are observed especially for polar compounds like amines, and at low
temperatures and concentrations.
SPECIALTY TUBES
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Connections:
Tube Data Sheet
VOC Zeroing Tube No. 025-2000-010
This tube is used to purify ambient air to form a zero standard for calibrating VOC
detectors in ambient background. Calibration should be performed at the same
temperature, humidity and ow as the measurement. To connect to a ppbRAE
3000, MiniRAE 3000 and MultiRAE Pro, use Inlet Tube Adapter p/n 025-3002-000
according to the instructions on the reverse side. See Technical Notes 150, 172
and 178 for more details on use and how to connect other monitors.
^ Measured with ppbRAE Plus after 2-minexposure (methane measured with an LEL sensor).
* This tube can not remove methane, ethane or ethylene.
Apparent Reading
(ppbv)^
Flex- I- Prob e
(p/n 023-3012-000)
Tube Adapter
(p/n 025-3002-000)
Tube Tip Breaker
VOC Zeroing Tube
(10-pack, p/n 025-2000-010)
Connection to MiniRAE Plus 2000 or ppbRAE
Tube Adapter
(p/n 025-3002-000)
Water Trap Adapter
(10-pack, p/n 025-3002-000)
4mm o.d. Teon™ tubing
tip cut at an angle
(p/n 025-3002-000)
Connection to Multi Gas monitors
Zeroing Procedure:
1) Insert the tip of the Flex-I-Probe or other probe into the smaller end of
the Tube Adapter.
2) Break the two ends of a VOC zeroing tube using the smaller hole on the
side of the Tube Adapter.
3) Insert one end (black arrow indicates the right direction) of the open
VOC zeroing tube into the bigger end of the adapter.
4) Run the zeroing calibration procedure of the instrument.
5) Discard the used VOC zeroing tube (single use only).
SPECIALTY TUBES
Cautions:
• Single use only
• Attach tube shortly before zeroing to avoid loss of adsorption capacity.
• Will not absorb CO; partially absorbs H2S. May not absorb some other
inorganic compounds.
SPECIALTY TUBES
• The contents of the tubes are non-hazardous, but may absorb hazardous
components from the sample gas.
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Tube Data Sheet
VOC/CO2 Zeroing Tube No. 025-2003-010
This tube is used to purify ambient air to form a zero standard for calibrating both CO2 &
VOC sensors in ambient background. Calibration should be performed at the same
temperature, humidity and ow as the measurement. To connect to an instrument,
use Inlet Tube Adapter p/n 025-3002-000 according to the instructions on the reverse
side. See Technical Notes 172 and 178 for more details on use and how to connect
other monitors. This tube contains the same VOC zeroing layer as tube 025-2000-
010 with an additional CO
Storage Life: 3 years
Temperature Range: -10 to +50°C
VOC Filtering Capacity:
CompoundConcentration
Methane1000010000*
Ethylene100000100000*
Propane1000000
Butane100000
Isobutylene1000000
Butadiene100000
n-Hexane100000
Gasoline100000
Toluene100000
Ethanol1000000
Acetone1000000
Ethylene oxide100000
Benzene100000
^ Measured with ppbRAE Plus after 2-minexposure (methane measured with an LEL sensor).
* This tube can not remove methane, ethane, or ethylene (methane measured with an LEL sensor).
SPECIALTY TUBES
It does not absorb CO and some other inorganic compounds, and partially absorbs H2S.
CO
Absorption
2
Reaction Principle: 2OH- + CO2 → H2O + CO
absorbing layer.
2
(ppbv)
Apparent
Reading
(ppbv)^
2-
3
Continued on next page
Table2. CO2 Absorption Capacity at 500 ppm CO
2
RH (%)Breakthrough time (min @ 500 cc/min)
>9514
~5018
<510
Note: The data in Table 2 were generated in ambient air with 500 ppm CO
At higher concentrations, the breakthrough time will decrease.
Connections:
Flex- I- Prob e
(p/n 023-3012-000)
Tube Adapter
(p/n 025-3002-000)
Tube Tip Breaker
VOC Zeroing Tube
(10-pack, p/n 025-2000-010)
Connection to handled PID monitors
Tube Adapter
(p/n 025-3002-000)
4mm o.d. Teon
Water Trap Adapter
(10-pack, p/n 025-3002-000)
™
tip cut at an angle
(p/n 025-3002-000)
tubing
Connection to Multi-gas monitors
Zeroing Procedure
1) Insert the tip of the probe into the smaller end of the Tube Adapter.
2) Break the two ends of a VOC/CO
zeroing tube using the smaller hole on the
2
side of the Tube Adapter.
3) Insert one end (black arrow indicates the right direction) of the open VOC/CO
zeroing tube into the wider end of the adapter.
4) Run the zero calibration procedures of the instrument for both VOC and CO
is preferable to zero the CO
is often greater than for CO
5) Discard the used VOC/CO
sensor rst because the tube’s capacity for VOCs
2
.
2
zeroing tube.
2
2
Cautions:
• Single use only.
• Attach tube shortly before zeroing to avoid loss of adsorption capacity.
. It
.
2
SPECIALTY TUBES
2
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Tube Data Sheet
Humidity Filtering II No. 025-2002-010
This tube is used to remove ambient humidity when connected to RAE Systems
pumped monitors. It is particularly useful for reducing humidity effects when
measuring VOCs with photoionization detectors (PIDs). At a ow rate of 500 cc/min,
the relative humidity is reduced to <10% until breakthrough. To connect the tube,
the instrument is tted with a Flex-I-Probe (p/n 023-3012-000) and tube adapter (p/n
025-3002-000). The tube has no effect on volatile, non-polar compounds such as
isobutylene, hexane, benzene, and trichloroethylene (see Table 2), but may affect
other compounds. See RAE Systems Technical Note 178 for more details.
CAUTION: The tube may delay or reduce the response of polar, heavy,
and reactive compounds and therefore due caution should be used when
measuring such compounds (see Table 2). Contact RAE Systems Technical
Support if the compound of interest is not in Table 2.
CAUTION: Response time effects depend on concentration, with more
signicant absorption losses at lower concentrations (see Table 2).
CAUTION: Not for use in unknown chemical environments such as HazMat
Response. A false low or zero reading may result.
NOTE: Use tubes within 1 hour of opening to avoid loss of humidity capacity.
Temperature Range: -20 to +50°C
Storage Life: 3 years
Color Change: White powder forms a glassy gel when moist
Table 1. Humidity Filtering Capacity
T
(°C)T (°F)
4511 3991214
401041001820
30861002226
206810023
SPECIALTY TUBES
RH
(%)
(min @ 500 cc/min)
75
50
25
75
50
75
50
75
50
Run time to t10
Note: The contents of the tubes are non-hazardous, but may absorb hazardous
components from the sample gas.
CF = Correction Factor. Multiply by reading to get true concentration to correct for some loss.
* Not recommended because of severe losses.
Note: The data in Table 2 were generated in dry air at about 22°C (72°C). Tests showed that
50% RH does not affect the response time to isobutylene, benzene, PGMEA, dimethyl sulde,
phenol, acetone or ethanol, but causes total loss of ammonia. 80% RH does not affect the
response time of isobutylene, benzene, or H
not signicantly different between a fresh tube and a partially used tube up to 20% humidity
breakthrough.
Other compounds: Volatile ethers, esters, haloalkanes, and olens should not be affected
except for possible slower response. Glycols, aldehydes and alcoholamines are expected to
have slower and/or lower response. Acids and bases may be lost on the tube. Compounds that
hydrolyze easily, such as acetic anhydride, isocyanates, or hexamethydisilazane may be lost.
(propylene glycol methyl ether acetate)10222401.1
Conc.
(ppm)T (°C)
S. The response time for polar compounds is
2
t
(sec)CF
90
#
(1.05)
SPECIALTY TUBES
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7 APPENDICES
7.1 Appendix 1. Alphabetical Tube List
Compound
Acetone10-111-400.1- 2%0.05 - 4%1 x 2
Amines10-132-100.5 - 100.25 - 201 x 1
Ammonia10-100-051 - 300.5 - 601 x 1.5
Benzene10-101-010.5 - 100.25 - 303 x 3
1,3-Butadiene 10-135-040.5 - 50.25 - 102 X 2
Butane10-137-3025 - 140012.5 – 28001 x 2.5
Carbon Dioxide10-104-30300 - 5000150 - 100001 x 2
Carbon Monoxide10-102-185 - 1002.5 - 2003 x 3
Chlorine10-106-100.5 - 80.25 - 161 x 2.5
Chlorine Dioxide10-130-100.25 - 150.05 - 301 x 2
Diesel & Jet Fuel10-143-100.25 - 25N/A4 x 1.5
Ethanol10-141-30100 - 200050 - 20001 x 3
Formaldehyde10-121-050.1 - 50.1 - 405 x 2
Gasoline10-138-3030 - 100015 - 20002 x 2
Hydrocarbons10-110-3050 - 100025 - 20002 x 2
Hydrogen Chloride10-108-091 - 200.5 - 401 x 1
Hydrogen Cyanide10-126-102.5 - 601.25 - 1202 x 2.5
SPECIALTY TUBES
Hydrogen Fluoride10-105-100.5 - 200.25 - 404 x 0.5
Hydrogen Sulde10-103-040.2 - 30.1 - 61 x 1.5
Tube
Number
10-100-105 - 1002.5 - 2001 x 1
10-100-1210 - 2605 - 5201 x 1.5
10-100-1525 - 50012 - 10001 x 1
10-100-401 - 15%0.5 - 30%1 x 2
10-101-105 - 4025 - 2005 x 3
10-101-205 - 1002.5 - 2001 x 2
10-104-400.05 - 1%0.025 - 2%1 x 2
10-104-450.25 - 3%0.12 - 6%1 x 2
10-104-501 - 20%0.25 - 20%0.5 x 1
10-104-605 - 40%1.25 - 40%0.5 x 1
10-102-205 - 1002.5 - 2001 x 2
10-102-3020 - 50010 - 10001 x 1.5
10-102-450.2 - 4%0.05 - 4%0.5 x 1
10-106-205 - 1002.5 - 2001 x 2
10-108-101 - 200.5 - 401 x 1
10-108-2220 - 50010 - 10001 x 1.5
10-103-05
Standard
Range
(ppmv unless
noted)
0.2 - 30.1 - 61 x 2
Total Meas.
Range
(ppmv unless
noted)
Standard Meas.
Time
(Strokes x min.
per stroke)
APPENDICES
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Appendix 1 (Continued). Alphabetical Tube List
Compound
Hydrogen Sulde
(cont.)
APPENDICES
Mercaptans10-129-205 - 1202.5 - 2401 x 2
Methyl Bromide10-131-101 - 180.5 - 362 x 3
Methyl Ethyl Ketone10-113-200.02 - 0.6%0.01 - 1.8%3 x 2
Nitric Acid10-146-201 - 200.5 - 401 X 1
Nitrogen Dioxide10-117-100.5 - 30N/A1 x 1.5
Nitrogen Oxides10-109-201 - 500.5 - 1001 x 3
Ozone10-133-030.05 - 0.60.05 - 1.8 5 x 2
Phenol10-139-051 - 250.5 - 1802 x 1.5
Phosphine10-116-105 - 502.5 - 1002 x 1.5
Sulfur Dioxide10-107-152 - 301 - 602 x 2
Toluene10-114-2010 - 3005 - 6001 x 2
Trichloroethylene10-119-205 - 1002.5 - 2301 x 3
Vinyl Chloride10-128-101 - 200.5 - 40 1 x 3
Water Vapor10-120-102-10 lbs/MMCF 1-20 lbs/MMCF2 x 1.5
7.7 Appendix 7. Other RAE Systems
Gas Detection Products
RAE Systems offers a broad array of products used to detect and measure
a wide variety of dangerous atmospheric contaminants and conditions
such as combustible gas and vapor accumulations, oxygen deciencies,
radiation, and toxic gases including carbon monoxide, hydrogen sulde,
carbon dioxide, and many other commonly encountered atmospheric
hazards. RAE Systems’ proprietary, patent-protected technology has made
it the world’s leading manufacturer of instruments equipped with portable
photoionization detectors (PIDs). RAE Systems’ PIDs allow dependable,
linear readings for many toxic gases and vapors in the low parts-perbillion to thousands of parts-per-million range, and are particularly well
suited for the measurement of volatile organic compounds such as
gasoline, benzene, paints, degreasers, jet fuel, and most organic solvents.
The company’s products are used in weapons of mass destruction
(WMD), environmental, safety, HazMat, toxic industrial chemical (TIC),
petrochemical, semiconductor, and conned space entry applications.
Complete data sheets and other information on all RAE Systems products
can be found at the RAE Systems web site, http://www.raesystems.com.
APPENDICES
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7.8 Appendix 8. Limited Product Warranty
RAE Systems Inc. (RAE) warrants manual (hand-operated) pumps to be
free of defects in workmanship for the life of use by the original owner. All
other consumable items such as inlet lters, rubber inlets, plunger gaskets,
which by their nature are consumed or depleted during normal operation,
are excluded from this standard warranty.
APPENDICES
RAE’s obligation under this warranty is limited to replacing or repairing,
at RAE’s option, any defective or damaged part if returned to a RAE
authorized factory repair center, with shipping charges prepaid by the
buyer.
To maintain warranty, Purchaser must perform maintenance and calibration
as prescribed in the Operation and Maintenance manual. In the event
of a defect or damage, Purchaser will notify a RAE designated factory
repair center in advance and if trouble diagnosis procedures are unable
to determine and remedy the condition, a Return Material Authorization
(RMA) will be issued to assure proper repair and logistics tracking.
RAE neither assumes nor authorizes any other rm or person to assume
on RAE’s behalf any liability in any way connected with the sale of RAE
products.
Warranty does not extend to any equipment malfunction or damage that
results from alteration, theft, misuse, abuse, abnormal use, or improper or
unauthorized repairs.
7.9 Appendix 9. RAE Systems Contacts
RAE Systems World Headquarters
3775 N. First St.
San Jose, CA 95134-1708 USA
Phone: 408.952.8200
Fax: 408.952.8480
E-mail: customerserv@raesystems.com
Web Site: www.raesystems.com
RAE Systems Technical Support
Monday through Friday, 7:00AM to 5:00PM Pacic Time
Life-critical after-hours support is available
+1.408.952.8200, select option 9
APPENDICES
This express warranty shall extend to buyer of record only and not to
sales made by buyer’s customers. Except for the warranty of title, the
foregoing express warranty is in lieu of any and all other warranties,
whether expressed or implied, including the implied warranties of tness
for a particular purpose and merchantability. Seller’s liability under the
warranty provided herein exclusive of insurance process shall be limited
to a refund of purchase price.
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GAS DETECTION
TUBES AND SAMPLING
HANDBOOK
Second Edition
TB -1001- 02
Real-time gas detection
For real-time decisions
www.raesystems.com
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