GB/T 24396-2009Test Method of Adsorption Resin for Food Industrial Use (English PDF)
食品工业用吸附树脂产品测定方法
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Issued by
General Administration of Quality Supervision, Inspection and Quarantine
Level / Type
National · Recommended
Issue date
September 30, 2009
Implementation date
December 1, 2009
Scope
GB/T 24396-2009 is the English-translated version of 食品工业用吸附树脂产品测定方法.
GB/T 24396-2009 — This Standard specifies the test method of adsorption resin for food industrial use.
This Standard applies to the determination of appearance, heavy metals and organic residues in adsorption resin for food industrial use that is copolymerized under the action of initiator, of which, the polymeric monomer is styrene, divinylbenzene, acrylics, acrylonitrile, and the pore-foaming agent is toluene or liquid paraffin.
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Document preview — GB/T 24396-2009
National Standard of the People's Republic of China
- ICS
- 67.250
- Classification
- G 31
Issued by: General Administration of Quality Supervision, Inspection and Quarantine
Contents
- Foreword...3
- 1 Scope...4
- 2 Method summaries...4
- 3 Reagents and materials...4
- 4 Instruments and equipment...5
- 5 Analysis steps...5
Foreword
Appendix A of this Standard is an informative appendix.
This Standard was proposed and managed by China National Institute of
Standardization.
The drafting organizations of this Standard. Tianjin Product Quality Supervision
and Testing Technology Research Institute.
Organizations that participate in the drafting of this Standard. Tianjin Ourui
Biological Technology Co., Ltd.
The drafters of this Standard. Bian Hui, Hong Yuchun, Liu Shuang, Tong Lili,
Ren Lihua, Ou Lailiang, Wu Qian, Yang Jialing.
Test Method of Adsorption Resin
for Food Industrial Use
1 Scope
This Standard specifies the test method of adsorption resin for food industrial
use.
This Standard applies to the determination of appearance, heavy metals and
organic residues in adsorption resin for food industrial use that is copolymerized
under the action of initiator, of which, the polymeric monomer is styrene,
divinylbenzene, acrylics, acrylonitrile, and the pore-foaming agent is toluene or
liquid paraffin.
2 Method summaries
2.1 Heavy metal detection
In the weak-acidic solution, sodium sulfide precipitates heavy metal ions into
the corresponding sulfides; the resulting color is visually compared to the
standard color.
2.2 Organic residue detection
The organic residue in the sample is ultrasonically extracted by absolute
ethanol; it is injected into the gas chromatograph and carried by the carrier gas
into the column for separation; the effluent is detected by a hydrogen flame
ionization detector; the content of organic residue is calculated according to the
external standard method.
3 Reagents and materials
WARNING. Some of the reagents which are used in this test method are
toxic or corrosive; therefore, some test procedures may cause dangerous
conditions, and the operator shall take appropriate safety and health
measures.
3.1 Hydrochloric acid. analytical reagent.
3.2 Acetic acid solution. 1 + 4.
3.3 Sodium sulfide solution. 100 g/L.
4 Instruments and equipment
4.1 Oven.
4.2 Muffle furnace.
4.3 Water bath.
4.8 Centrifuge. 0 r/min ~ 4 000 r/min (adjustable).
4.9 Brown volumetric flasks. 100 mL, 50 mL, and 10 mL.
4.10 Pipette. 1 µL ~ 10 µL, 10 µL ~ 100 µL, 100 µL ~ 1 000 µL and 0.5 mL ~ 5
mL.
4.11 Pipette. 5 mL, 10 mL.
4.12 Needle filter. 0.45 µm.
5 Analysis steps
5.1 Determination of appearance
Place the sample in a clean white porcelain dish; place it in a bright place, and
visually inspect it under natural light.
5.2 Determination of heavy metal
5.2.1 Preparation of test solution
Weigh 2.0 g of sample (dry basis) which is dried at 105°C ± 2°C for 2 h; accurate
to 0.01 g; place it in the evaporating dish; carbonize it and then burn it at 500°C
± 25°C until the complete ashing; cool it; then, add 2 mL of hydrochloric acid;
5.2.2 Preparation of lead (Pb) standard colorimetric solution
Transfer 2 mL of acetic acid solution into a 50 mL colorimetric tube (matching
tube A); add 1.50 mL of lead standard solution; add water to 25 mL, which is
the tube B.
5.3 Determination of organic residue
5.3.1 Preparation of samples
Place 10 mL of the sample in a centrifuge tube; centrifuge at 2000 r/min ± 200
r/min for 5 min. Take the upper layer of the sample from which the surface free
water has been removed
5.3.2 Preparation of standard solution
5.3.2.1 Preparation of mixed standard solution mother solution
According to the order of styrene, o-xylene, m-xylene, p-xylene, chlorobenzene,
toluene, methyl methacrylate, divinylbenzene, 1,2-dichloroethane, benzene,
acrylonitrile, weight 0.1 g of each of the above standards (accurate to 0.000 1
g); place in a 100 mL brown volumetric flask; use absolute ethanol to dilute to
the mark; shake well.
5.3.3 Determination of standard series solution
Turn on the gas chromatograph and set the chromatographic conditions
according to Appendix A. After the baseline is stable, take the series standard
solutions which are prepared in 5.3.2.2 for injection analysis; record the peak
area of each time; draw the following standard curve.
5.3.4 Determination of the sample
Take the sample solution that is prepared in 5.3.1 for injection analysis; record
the chromatographic peak area; according to the concentration range of each
residue in the sample, substitute the appropriate standard curve to find the
corresponding residue mass concentration rho (µg/mL).
5.3.5 Calculation of analysis result
Calculate the content of residues in the sample according to Formula (1).
Appendix A
(Informative)
Organic residue determination reference gas chromatography operating
conditions
According to the used gas chromatograph, adjust the appropriate temperature
and flow rate to achieve the proper separation effect. Reference
chromatographic conditions are shown as below.
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This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 5 pages — is available in the English PDF.
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