GBZ/T 300.61-2017 PDF in English
GBZ/T 300.61-2017 (GBZ/T300.61-2017, GBZT 300.61-2017, GBZT300.61-2017)
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Determination of toxic substances in workplace air -- Part 61: Butylene, 1, 3-butadiene and dicyclopentadiene
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Standards related to (historical): GBZ/T 300.61-2017
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GBZ/T 300.61-2017: PDF in English (GBZT 300.61-2017) GBZ/T 300.61-2017
GBZ
NATIONAL OCCUPATIONAL HEALTH
STANDARD OF THE PEOPLE’S REPUBLIC OF CHINA
ICS 13.100
C 52
Replacing GBZ/T 160.39-2007
Determination of Toxic Substances in Workplace Air -
Part 61: Butylene, 1,3-Butadiene and Dicyclopentadiene
ISSUED ON: NOVEMBER 09, 2017
IMPLEMENTED ON: MAY 01, 2018
Issued by: National Health and Family Planning Commission of the
People’s Republic of China
Table of Contents
Foreword ... 3
1 Scope ... 5
2 Normative References ... 5
3 Basic Information of Butylene, 1,3-Butadiene and Dicyclopentadiene ... 5
4 Butylene Direct Injection - Gas Chromatography ... 6
5 1,3-Butadiene Solvent Desorption - Gas Chromatography ... 9
6 Dicyclopentadiene Solvent Desorption - Gas Chromatography ... 12
Determination of Toxic Substances in Workplace Air -
Part 61: Butylene, 1,3-Butadiene and Dicyclopentadiene
1 Scope
This Part of GBZ/T 300 specifies the butylene direct injection - gas chromatography,
and the 1,3-butadiene and dicyclopentadiene solvent desorption - gas chromatography
in workplace air.
This Part is applicable to the detection of the concentration of butylene, 1,3-butadiene
and dicyclopentadiene in the workplace air.
2 Normative References
The following documents are essential to the application of this document. For the
dated documents, only the versions with the dates indicated are applicable to this
document; for the undated documents, only the latest version (including all the
amendments) is applicable to this document.
GBZ 159 Specifications of Air Sampling for Hazardous Substances Monitoring in
the Workplace
GBZ/T 210.4 Guide for Establishing Occupational Health Standards - Part 4:
Determination Methods of Air Chemicals in Workplace
3 Basic Information of Butylene, 1,3-Butadiene and
Dicyclopentadiene
The basic information of butylene, 1,3-butadiene and dicyclopentadiene can refer to
Table 1.
b) Column temperature: 50°C;
c) The temperature of the gasification chamber: 150°C;
d) The temperature of the detection chamber: 150°C;
e) Carrier gas (nitrogen) flow rate: 40mL/min.
4.3 Reagents
4.3.1 Dibutyl phthalate and β, β’-oxydipropionitrile, chromatographic stationary liquid.
4.3.2 6201 red carrier, 60mesh~80mesh.
4.3.3 Butylene, the mass of 1mL of gas at 20°C is 2.33mg.
4.3.4 Standard gas: Before use, fill the empty drying tube with water and put it upside
down into a 500mL beaker containing water. The upper port of the drying tube is sealed
with a silicone rubber pad; and a section of rubber tube is covered; take a small amount
of water as water seal. Pass in pure butylene gas from the lower port of the drying tube
to replace the effluent. Use a syringe to take 1.0mL of butylene through the water seal
from the upper port of the drying tube. When the syringe needle is pulled out and pass
the water seal, a small amount of water is drawn to seal the extracted butylene. Inject
butylene into a 100mL airtight glass syringe; dilute it to 100.0mL by clean air; and
prepare the butylene standard gas. Or use an airtight syringe to accurately take a
certain amount of butylene; inject it into a 100mL airtight glass syringe; dilute it to
100.0mL by clean air; and prepare the butylene standard gas. Or use nationally
recognized standard gas to prepare.
4.4 Collection, transportation and storage of samples
4.4.1 On-site sampling shall be carried out in accordance with GBZ 159.
4.4.2 Short-time sampling: At the sampling point, clean the gas sampling bag by
sample air for 3~5 times; and then collect the sample air. After sampling, immediately
close the intake valve of the gas sampling bag; and place it in a clean container for
transportation and storage. The sample shall be measured within 24h.
4.4.3 Sample blank: Bring the gas sampling bag to the workplace; after collecting the
clean air, transport, store and measure it together with the sample. There are no less
than 2 sample blanks for each batch of samples.
4.5 Analysis procedures
4.5.1 Sample processing: Put the gas sampling bag that has sampled in the laboratory
of the determination standard series for determination.
5.3.4 Methylene chloride, chromatographic identification without interference peaks.
5.3.5 Standard solution: add about 2mL of methylene chloride into a 5mL volumetric
flask; and use an airtight syringe to inject a certain amount of 1,3-butadiene into the
methylene chloride; and use methylene chloride to make the constant volume.
Calculate the concentration of this solution from the amount of added 1,3-butadiene;
and it is the butadiene standard solution. Or use a nationally recognized standard
solution to prepare.
5.4 Collection, transportation and storage of samples
5.4.1 On-site sampling shall be carried out in accordance with GBZ 159.
5.4.2 Short-time sampling: At the sampling point, use an activated charcoal tube to
collect air samples for 15min at a flow rate of 200mL/min.
5.4.3 Long-time sampling: At the sampling point, use an activated charcoal tube to
collect air samples for 2h~8h at a flow rate of 50mL/min.
5.4.4 After sampling, immediately seal both ends of the activated charcoal tube and
place it in a clean container for transportation and storage. The samples can be stored
in a refrigerator at 4°C for 7d.
5.4.5 Sample blank: At the sampling point, open both ends of the activated charcoal
tube and immediately seal it; and then transport, store and measure together with the
sample. There shall be no less than 2 sample blanks in each batch of samples.
5.5 Analysis procedures
5.5.1 Sample processing: Pour the sampled active charcoal into two solvent desorption
bottles, respectively; add 1.0mL of methylene chloride to each; after sealing, desorb
for 30min; shake from time to time. The sample solution is available for determination.
5.5.2 Drawing of standard curve: Take 4~7 pieces of volumetric flasks; and use
methylene chloride to dilute the standard solution to form a standard series of 1,3-
butadiene with a concentration range of 0.0µg/mL~620.0µg/mL. Refer to the operating
conditions of the instrument; adjust the gas chromatograph to the best measurement
state; inject a sample of 1.0µL; and respectively measure the peak height or peak area
of each concentration of each standard series. Draw a standard curve or calculate a
regression equation with the measured peak height or peak area versus the
corresponding 1,3-butadiene concentration (µg/mL); and the correlation coefficient
shall be ≥0.999.
5.5.3 Sample determination: Use the operating conditions for determining the standard
series to determine the sample solution and sample blank solution; and according to
the measured peak height or peak area value, the concentration of 1,3-butadiene in
determination. Constant temperature measurement or programmed temperature-rise
measurement can be selected according to the measurement needs.
6 Dicyclopentadiene Solvent Desorption - Gas
Chromatography
6.1 Principle
The vaporized dicyclopentadiene in the air is collected by activated charcoal, and the
sample is injected after carbon disulfide desorption, separated by a gas
chromatographic column, and detected by a hydrogen flame ionization detector; so
that retain the retention time qualitative, and peak height or peak area quantitative.
6.2 Apparatus
6.2.1 Activated charcoal tube, solvent desorption type, contain 100mg/50mg of
activated charcoal.
6.2.2 Air sampler, the flow rate range is 0mL/min~500mL/min.
6.2.3 Solvent desorption bottle, 5mL.
6.2.4 Micro syringe.
6.2.5 Gas chromatograph equipped with hydrogen flame ionization detector.
Reference conditions for instrument operation are as follows:
a) Chromatographic column: 30m×0.32mm×0.5µm, FFAP;
b) Column temperature: 130°C;
c) The temperature of the gasification chamber: 180°C;
d) The temperature of the detection chamber: 180°C;
e) Carrier gas (nitrogen) flow rate: 1mL/min;
f) Split ratio: 10:1.
6.3 Reagents
6.3.1 Carbon disulfide, chromatographic identification without interference peaks.
6.3.2 Dicyclopentadiene, the mass of 1μL of liquid at 20°C is 0.980mg.
6.3.3 Standard solution: Add carbon disulfide to the volumetric flask; and after accurate
weighing, use a micro syringe to draw a certain amount of dicyclopentadiene into the
carbon disulfide; then accurately weigh it; and use carbon disulfide to make the
constant volume. Calculate the concentration of the solution from the difference
between the two weighings. Dilute with carbon disulfide to make 1000.0μg/mL
dicyclopentadiene standard solution. Or use a nationally recognized standard solution
to prepare.
6.4 Collection, transportation and storage of samples
6.4.1 On-site sampling shall be carried out in accordance with GBZ 159.
6.4.2 Short-time sampling: At the sampling point, use an activated charcoal tube to
collect air samples for 15min at a flow rate of 200mL/min.
6.4.3 Long-time sampling: At the sampling point, use an activated charcoal tube to
collect air samples for 2h~8h at a flow rate of 30mL/min.
6.4.4 After sampling, immediately seal both ends of the activated charcoal tube and
place it in a clean container for transportation and storage. The sample can be stored
for 7d at room temperature.
6.4.5 Sample blank: At the sampling point, open both ends of the activated charcoal
tube and close it immediately; and then transport, store and measure it together with
the sample. There shall be no less than 2 sample blanks for each batch of samples.
6.5 Analysis procedures
6.5.1 Sample processing: Pour the sampled former and latter sections of active
charcoal into two solvent desorption bottles, respectively; add 1.0mL of carbon
disulfide to each; after sealing, desorb for 30min; shake from time to time. The sample
solution is available for determination.
6.5.2 Drawing of standard curve: Take 4~7 pieces of volumetric flasks; use carbon
disulfide to dilute the standard solution to form dicyclopentadiene standard series in
the concentration range of 0.0µg/mL~700.0µg/mL. Refer to the operating conditions of
the instrument; adjust the gas chromatograph to the best measurement state; inject a
sample of 1.0µL; and respectively measure the peak height or peak area of each
concentration of the standard series. Draw a standard curve or calculate a regression
equation with the measured peak height or peak area versus the corresponding
dicyclopentadiene concentration (µg/mL); and the correlation coefficient shall be
≥0.999.
6.5.3 Sample determination: Use the operating conditions for determining the standard
series to determine the sample solution and sample blank solution; and according to
the measured peak height or peak area value, obtain the concentration of
dicyclopentadiene in the sample solution (µg/mL) from the standard curve or
......
Source: Above contents are excerpted from the PDF -- translated/reviewed by: www.chinesestandard.net / Wayne Zheng et al.
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