GB/T 24572.6-2026Standard practice for the separation and concentration of ignitable liquid residues from fire debris samples - Part 6: Thermal desorption (English PDF)
火灾现场易燃液体残留物实验室提取方法 第6部分:热脱附法
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Issued by
SAMR; SAC
Level / Type
National · Recommended
Issue date
April 30, 2026
Implementation date
November 1, 2026
Scope
GB/T 24572.6-2026 is the English-translated version of 火灾现场易燃液体残留物实验室提取方法 第6部分:热脱附法.
GB/T 24572.6-2026 is the Chinese national standard covering recovering traces of an accelerant from fire debris by thermal desorption - heating the adsorbent that captured the vapours and releasing them straight into the chromatograph, which loses less of the sample than solvent extraction. This is arson investigation at the bench. Part 6 of the series, first edition of this part, in force since 1 November 2026. It was issued on 30 April 2026 and takes effect on 1 November 2026, as a first edition. The document is under the responsibility of the National Fire and Rescue Administration. This page is published from the official record of the 2026 edition; the clause text of a standard this recent is not yet in circulation, and the figures, limits and tables it contains are those of the document itself, delivered in full with the English translation.
Document preview — GB/T 24572.6-2026
National Standard of the People's Republic of China
- ICS
- 13.220.01
- Classification
- C 82
Issued by: State Administration for Market Regulation; Standardization Administration of the PRC
Contents
- 4 Principles and Characteristics
- 5 Materials and Equipment
- 5.2 Container Material
- 6 Thermal Desorption
- 6.2 Sealing of the sample
- 6.3 Adsorption
- 6.3.3 Dynamic Adsorption
- 6.4 Thermal Desorption
- 6.4.1 Thermal desorption method
- 6.4.2 Thermal desorption conditions
Foreword
This document complies with the provisions of GB/T 1.1-2020 "Standardization Work Guidelines Part
1.Structure and Drafting Rules of Standardization Documents". Drafting. This document is Part 6 of GB/T 24572 "Laboratory Extraction Methods for Flammable Liquid Residues from Fire Scenes". GB/T 24572 has been... The following sections have been published.
1.Solvent Extraction Method;
2.Direct Headspace Sampling;
3.Activated Carbon Adsorption Method;
4.Solid-Phase Microextraction;
5.Sweeping and Trapping Method;
6.Thermal Desorption. Please note that some content in this document may involve patents. The issuing organization of this document assumes no responsibility for identifying patents. This document was proposed by the National Fire and Rescue Administration. This document is under the jurisdiction of the National Fire Protection Standardization Technical Committee (SAC/TC113). This document was drafted by: Tianjin Fire Research Institute, Ministry of Emergency Management; Shenyang Fire Research Institute, Ministry of Emergency Management; and Shanghai Fire Research Institute, Ministry of Emergency Management. Research Institute, Sichuan Fire Research Institute of the Ministry of Emergency Management, Henan Provincial Fire and Rescue Corps, Hunan Provincial Fire and Rescue Corps, Tsinghua University Hefei Public Security The entire research institute and the Tianjin Fire and Rescue Corps. The main drafters of this document are. Tian Guihua, Fan Zilin, Deng Zhenyu, Liang Guofu, Guo Ge, Liu Shujun, Huang Hao, Zhang Yi, Su Wenwei, and Liu Haiyan. Li Changzheng and Guo Lei.
Identifying flammable liquid residues at a fire scene is crucial for determining whether arson is suspected. This includes the laboratory extraction of samples. Quantity is a key factor affecting the accuracy of identification conclusions. To standardize this type of physical evidence identification work, a system has been established within my country's fire investigation standard system. Standard for laboratory pretreatment methods for fire evidence. GB/T 24572, "Laboratory Extraction Methods for Flammable Liquid Residues at Fire Scenes," is proposed to consist of six parts.
1.Solvent Extraction Method. This method aims to address the extraction of high-boiling-point substances and soot samples.
2.Direct Headspace Sampling. This method is designed for extracting residues of low-boiling-point flammable liquids.
3.Activated Carbon Adsorption Method. The purpose is to address flammable liquid residue samples that can be selectively adsorbed by activated carbon. extract.
4.Solid-Phase Microextraction. The aim is to address flammable liquids that can be selectively adsorbed by solid-phase microextraction fiber coatings. Extraction of residue samples.
5.Purge and Trap Method. This method is designed for extracting flammable liquid residues with high water content.
4 Principles and Characteristics
4.1 Principle Sample tubes containing the evidence, or sample tubes adsorbed with flammable liquid from the evidence, are placed on a thermal desorption instrument and directly heated for desorption. Flammable liquid enters a low-temperature cold trap along with the carrier gas. The cold trap is rapidly heated to a high temperature, and the desorbed and vaporized flammable liquid is then transported along with the carrier gas through a constant-temperature transfer line. The sample is then subjected to gas chromatography-mass spectrometry for detection.
4.2 Characteristics Thermal desorption has the following characteristics.
---Do not damage the appearance of the sample;
---Applicable to small-volume and fluffy evidence;
---Suitable for enrichment of trace amounts of flammable liquid residues.
5 Materials and Equipment
5.1 Carrier Gas Nitrogen gas with a purity of 99.9% or higher; high-purity helium gas with a purity of 99.999% or higher.
5.2 Container Material
5.2.1 Evidence Bag Including polyamide nylon, polyethylene terephthalate (PET), and polyethylene (PE). Evidence bags should be made of plastics such as ethylene (PE) and polyvinyl chloride (PVC). Evidence bags should ideally be airtight. Nylon and PET evidence bags.
5.2.2 Container Various types of containers with good airtightness. Containers should preferably have an air inlet at the bottom and an air outlet at the top, and be sealed with silicone rubber, fluororubber, or similar materials. A special metal container for the ring.
5.3 Adsorbent Materials Adsorbent materials include.
a) Dry powder fire extinguishing agents, diatomaceous earth, and other micron-sized high specific surface area fine powders with a specific surface area of 10m^2/g to 300m^2/g;
b) Soft, porous materials such as plant fibers, hair, oil-absorbing cotton, activated charcoal, or activated charcoal fibers;
c) Polydimethylsiloxane (PDMS), divinylbenzene (DVB), and other polymers Solid-phase microextraction fibers and films with coatings.
5.4 Sample Tubes This includes empty stainless steel tubes and adsorption tubes filled with adsorbent packing material. The adsorbent packing material should preferably be poly(2,6-diphenyl-p-phenylene ether) (Tenax- TA) and poly(2,6-diphenyl-p-phenyl ether) containing 30% graphitized carbon black (Tenax-GR).
5.5 Sampler This includes syringes and sampling pumps with a volume of at least 50 mL. Small-volume sampling pumps with flow control functionality are preferred.
5.6 Heating Equipment For ovens or other heating equipment with temperature control functions, the heating temperature should be between 40°C and 100°C.
5.7 Aging device The technical requirements for aging sample tubes in an aging device shall meet the following criteria.
---The set temperature should not be lower than 400°C;
---The carrier gas flow rate is adjustable, and the maximum carrier gas flow rate should not be less than 100 mL/min.
5.8 Thermal Desorption Instrument Manual loading of the thermal desorption unit or fully automatic thermal desorption unit.
5.9 Gas Piping System Gas lines and related accessories used to connect thermal desorption instruments and gas chromatograph-mass spectrometers.
6 Thermal Desorption
1.Scope This document describes the characteristics of the laboratory-based thermal desorption method, and the materials and equipment used for extracting flammable liquid residues from fire scenes. and experimental procedures. This document applies to the enrichment and desorption of flammable liquids such as gasoline, kerosene, diesel, and paint thinner remaining at fire scenes in the laboratory. He used it as a reference for the enrichment and desorption of volatile substances and thermal decomposition products of polymer materials.
3.Terms and Definitions This document does not contain any terms or definitions that need to be defined.
6.2 Sealing of the sample
6.2.1 Static Adsorption Sealing Sealing steps for static adsorption method.
a) Place the sample in an evidence bag, suspend the absorbent tube or absorbent material inside the bag, and then seal it;
b) Place the sample into the container, suspend the adsorption tube or adsorption material on the container lid, and then close and seal it.
6.2.2 Dynamic Adsorption Sealing Sealing steps for dynamic adsorption method.
a) The evidence was placed in a sealed bag. 1) Place the sample in a bag, tie the bag tightly, preferably by folding the edges of the bag opening in half and then binding it, or by using a special tool strip to lock it securely; 2) Connect the air inlet end of the adsorption tube to the evidence bag. Place the evidence bag horizontally, insert the air inlet end of the adsorption tube into the evidence bag, and cut it open. Insert it into the small opening or the special air outlet of the evidence bag and lock it tightly, keeping the air outlet of the adsorption tube sealed.
b) Sealed container. 1) Place the sample into a special container with an air inlet at the bottom and an air outlet at the top, and seal it. 2) Insert the air inlet end of the adsorption tube into the air outlet of the container and lock it in place, keeping the air outlet end of the adsorption tube sealed.
6.3 Adsorption
6.3.1 General Requirements This includes static adsorption and dynamic adsorption, both of which are optional. Static adsorption should be used when the sample clearly shows a positive result for flammable liquids, except... In addition, all samples should be subjected to dynamic adsorption.
6.3.2 Static Adsorption This includes adsorption under volatilization equilibrium conditions at room temperature or under heating volatilization equilibrium conditions. The ideal time for room temperature equilibrium is approximately [time value missing]. 30 min; the heating equilibrium conditions should be a heating temperature of 40°C~70°C and an equilibrium time of about 20 min.
6.3.3 Dynamic Adsorption
6.3.3.1 Negative pressure adsorption (sampling pump adsorption) Connect the outlet end of the adsorption tube, which has undergone dynamic adsorption sealing (see 6.2.2), to the sampling pump for negative pressure adsorption (sampling pump adsorption). After attachment, remove the adsorption tube and quickly seal both ends of the adsorption tube. The adsorption time depends on the volume of the container material and the concentration of the target substance remaining in the flammable liquid; the carrier gas flow rate should be 20 mL/min. 100 mL/min. When the flammable liquid content of the sealed evidence bag is low, sampling should continue until the evidence bag shows slight wrinkles; for evidence in sealed containers, room temperature sampling is recommended. Under suitable conditions, the sampling pump should be used for adsorption. If the content of flammable liquid in the sample is low, a temperature of 40°C~70°C and an equilibration time of approximately 20 minutes are recommended. After heating mode, the sampling pump adsorption is performed.
6.3.2.2 Positive pressure adsorption Positive pressure adsorption includes the following two adsorption methods.
a) Injection adsorption. Use a syringe to draw gas from the sealed container, remove the sealing plugs at both ends of the adsorption tube, and inject the gas along the gas inlet direction on the adsorption tube. Introduce the gas and quickly seal both ends of the adsorption tube after adsorption is complete.
b) Purge adsorption. Remove the plug from the outlet end of the adsorption tube at the top of the container, open the nitrogen purging inlet at the bottom of the container, and allow nitrogen to flow through the sample. The gas then enters the adsorption tube to complete positive pressure adsorption; the purging conditions should be nitrogen flow rate of 10 mL/min to 100 mL/min and heating temperature of 40°C~70°C, purging time 10min~60min; after adsorption is complete, remove the adsorption tube and quickly seal both ends of the adsorption tube. When the sample contains a high moisture content, rapid backflushing should be used to remove the moisture from the adsorption tube. Connect the outlet end of the adsorption tube to a gas... With the gas source and inlet open, initiate gas purging. The backflushing condition should ideally use nitrogen, with a gas flow rate of 100 mL/min to 500 mL/min and a purging duration of 30s~90s.
6.4.1 Thermal desorption method
6.4.1.1 Direct Desorption Fill both ends of an empty stainless steel tube with a small amount of glass wool, and place a tiny piece of evidence with a diameter of less than 4 mm in the middle. Fine powder samples are suitable for this method. The fabric is wrapped into a strip with a diameter of less than 4 mm. The sample tube containing the sample is then transferred to a thermal desorption apparatus for desorption.
6.4.1.2 Desorption of Adsorbent Material A small amount of glass wool is filled at both ends of a stainless steel tube, and adsorption material that has undergone static or dynamic adsorption treatment is placed in the middle. The tube containing the adsorption material is then placed... The sample tube of the material was transferred to a thermal desorption apparatus for desorption.
6.4.1.3 Desorption of Adsorption Tubes The adsorption tubes, after static headspace or dynamic adsorption, are transferred to a thermal desorption apparatus for desorption.
6.4.2 Thermal desorption conditions
6.4.2.1 Sample tube desorption analysis Desorption and desorption temperature selection.
---Organic samples. biological materials, textiles, plastics, and rubber, etc., preferably at temperatures below 100°C;
---Inorganic samples. soil, tiles, cement blocks, etc., should be kept at a temperature below.200°C;
---Adsorption materials. Activated carbon (temperature should be 150°C~200°C), extraction fibers or films coated with PDMS, DVB polymers, etc. The ideal temperature is.200°C~260°C.
---Adsorption tube. The desorption temperature should be set according to the manufacturer's recommended temperature. The desorption thermal desorption time should be 3 min to 50 min.
6.4.2.2 Cold Trap Focusing The temperature should generally be below 10°C. When there is a clear positive result or a high content of flammable liquid residue, the temperature should be 25°C and the time should be 3 minutes.
6.4.2.3 Flow split ratio Depending on the enrichment concentration, split ratios of 40.1, 20.1, and no splitting are used. When using the splitting mode, a trap can be selected... A staged desorption (TrapDesorb) or tube desorption (TubeDesorb) split can be selected, or a single-stage split can be chosen. A single-stage split can be selected. When using this method, it is advisable to adopt the Trap-Desorb split mode to ensure good peak shape and improved sensitivity.
6.4.2.4 Other Recommended Conditions Other recommended conditions include, but are not limited to.
---The flow rate of the high-purity helium carrier gas is 40 mL/min;
---Transmission line temperature is 150°C~200°C;
---The cold trap heating rate is the maximum rate.
Note. Select the optimal desorption conditions according to the different types of instruments.
6.5 Testing The sample obtained after thermal desorption extraction should be tested for the target analyte. For common flammable liquids, the testing should be performed according to GB/T 18294.5. For other volatile flammable liquids, the requirements of GB/T 19267.7 shall apply.
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This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 17 pages — is available in the English PDF.
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Related Standards
GB/T 24572.1-2009 — Standard practice for separation and concentration of ignitable liquid residues from fire debris samples - Part 1: Solvent extraction
GB/T 24572.2-2009 — Standard practice for separation and concentration of ignitable liquid residues from fire debris samples - Part 2: Direct headspace vapors sampling
GB/T 24572.3-2009 — Standard practice for separation and concentration of ignitable liquid residues from fire debris samples - Part 3: Activated charcoal absorption
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