GB 5009.212-2016_English: PDF (GB5009.212-2016)
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Determination of diarrhetic shellfish poison in shellfish
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GB 5009.212-2016
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| GB/T 5009.212-2008 | English | 239 |
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Determination of diarrhetic shellfish poison in shellfish
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GB/T 5009.212-2008
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| Standard ID | GB 5009.212-2016 (GB5009.212-2016) | | Description (Translated English) | Determination of diarrhetic shellfish poison in shellfish | | Sector / Industry | National Standard | | Classification of Chinese Standard | X09 | | Word Count Estimation | 15,141 | | Date of Issue | 2016-12-23 | | Date of Implementation | 2017-06-23 | | Older Standard (superseded by this standard) | GB/T 5009.212-2008; SC/T 3024-2004; SN/T 1996-2007; SN/T 2131.1-2008; SN/T 2131.2-2010; SN/T 2269-2009 | | Regulation (derived from) | National Health and Family Planning Commission Notice No.17 of 2016 | | Standard ID | GB/T 5009.212-2008 (GB/T5009.212-2008) | | Description (Translated English) | Determination of diarrhetic shellfish poison in shellfish | | Sector / Industry | National Standard (Recommended) | | Classification of Chinese Standard | C53 | | Classification of International Standard | 67.040 | | Word Count Estimation | 6,622 | | Date of Issue | 2008-11-21 | | Date of Implementation | 2009-03-01 | | Quoted Standard | GB/T 6682; GB 14925 | | Drafting Organization | Ministry of Health Food Hygiene Supervision and Inspection | | Administrative Organization | Ministry of Health | | Regulation (derived from) | National Standard Approval Announcement 2008 No.22 (Total No.135) | | Proposing organization | People's Republic of China Ministry of Health | | Issuing agency(ies) | Ministry of Health of People's Republic of China; Standardization Administration of China | | Summary | This standard specifies the shellfish and their products in the determination of diarrhetic shellfish toxins. This standard applies to shellfish and their products-Determination of diarrhetic shellfish toxins. |
GB 5009.212-2016
NATIONAL STANDARD OF THE
PEOPLE’S REPUBLIC OF CHINA
National Food Safety Standard - Determination of
Diarrheic Shellfish Poison in Shellfish
ISSUED ON: DECEMBER 23, 2016
IMPLEMENTED ON: JUNE 23, 2017
Issued by: National Health and Family Planning Commission of the
People’s Republic of China;
China Food and Drug Administration.
Table of Contents
Foreword ... 3
1 Scope ... 4
Mouse Biology Method ... 4
2 Principle ... 4
3 Reagents and Materials ... 4
4 Instruments and Equipment ... 5
5 Analytical Procedures ... 5
6 Expression of Analytical Result ... 7
Enzyme Linked Immunosorbent Assay (ELISA method) ... 8
7 Principle ... 8
8 Reagents and Materials ... 8
9 Instruments and Equipment ... 9
10 Analytical procedures ... 10
11 Expression of Analytical Result ... 11
12 Others ... 11
Liquid Chromatography - Tandem Mass Spectrometry ... 12
13 Principle ... 12
14 Reagents and Materials ... 12
15 Instruments and Equipment ... 14
16 Analytical Procedures ... 14
17 Expression of Analytical Result ... 18
18 Precision ... 19
19 Others ... 19
Appendix A Evaluation Technical Parameters of Commercial Kit ... 20
Appendix B Virulence Factor of Diarrheic Shellfish Poison ... 21
Appendix C Multiple Reaction Monitoring Chromatogram of Diarrheic Shellfish
Poison Standard Solution ... 22
National Food Safety Standard - Determination of
Diarrheic Shellfish Poison in Shellfish
1 Scope
This Standard specifies mouse biology method, enzyme linked immunosorbent assay
(ELISA method) and liquid chromatography - tandem mass spectrometry for the
determination of diarrheic shellfish poison in shellfish.
In this Standard, mouse biology method and enzyme linked immunosorbent assay
(ELISA method) are applicable to the determination of diarrheic shellfish poison in
shellfish and shellfish products; liquid chromatography - tandem mass spectrometry is
applicable to the determination of diarrheic shellfish poison okadaic acid (OA),
dinophysistoxins-1 (DTX-1) and dinophysistoxins-2 (DTX-2) in edible part of shellfish
and shellfish products (excluding salted products).
Mouse Biology Method
2 Principle
Use acetone to extract diarrheic shellfish poison (DSP) in shellfish. Through the
distribution with anhydrous ether, decompression and evaporation, take saline solution,
which contains 1% Tween-60, as the dispersing medium, prepare DSP injectable
suspension. Inject the injectable suspension into mouse’s peritoneal cavity. Observe
the survival of the mouse; calculate its virulence.
3 Reagents and Materials
Unless it is otherwise stipulated, all reagents used in this Method shall be analytically
pure. Water shall be Grade-1 water stipulated in GB/T 6682.
3.1 Reagents
3.1.1 Acetone (C3H6O).
3.1.2 Anhydrous ether (C4H10O).
3.1.3 Tween-60 (C64H126O26).
3.1.4 Sodium chloride (NaCl).
5.2.2 Frozen sample
At room temperature, thaw frozen sample, till it displays semi-frozen state. In terms of
shelled frozen sample, in accordance with the methods in 5.2.1, wash, open the shell,
rinse and take out the shell meat; remove frozen pieces attached to the external part
of the shell meat; wipe off the moisture. Cut the shell meat into pieces.
5.3 Sample Extraction
Weigh-take 200 g of shell meat sample, which is already cut into pieces; place it in a
homogeneous cup. In accordance with the volume ratio, add a triple amount of acetone,
then, homogenize it for over 2 min. Pour the well-homogenized substance into a Brinell
funnel, then, extract and filter it; gather the filtrate. Respectively use acetone, which is
2 times the amount of the residue, to rinse the residue twice. Combine the filtrate and
the above-mentioned filtrate. Transfer the filtrate into a 500 mL of round-bottomed flask.
At 56 °C ± 1 °C, decompress and concentrate it to remove acetone, till greasy
substance is separated from the liquid surface.
Use 100 mL ~ 200 mL of anhydrous ether to dissolve the greasy substance; pour it
into a separating funnel. Use a small amount of anhydrous ether to rinse the round-
bottomed flask; combine them and pour them into the separating funnel. Use a small
amount of water to wash the lower sticky wall part. Slightly oscillate (avoid generating
emulsion); place it still for stratification. Then, remove the aqueous layer (the lower
layer).
Use water, which is equivalent to half the amount of ether, to wash the ether layer twice.
Remove the aqueous layer, then, transfer the ether layer into a 250 mL or 500 mL
round-bottomed flask. At 35 °C ± 1 °C, decompress and concentrate it to remove ether.
Use a small amount of anhydrous ether to transfer the concentrated substance into a
50 mL or 100 mL round-bottomed flask. Again, decompress and concentrate it to
remove ether.
Use 1% Tween-60 saline solution to transfer all the concentrated substance into a
scale test tube, then, dilute it into 10 mL. Thoroughly shake it to prepare a homogenous
suspension. 1 mL of the suspension is equivalent to 20 g of sample. Take this
suspension as test stock solution.
Use the test stock solution to inject mice. When within 24 h, 2 or 3 mice died, oscillate
the test stock solution, so that it could become homogenous suspension, then, use 1%
Tween-60 saline solution to step-by-step dilute it, in accordance with Table 1, into 4
times or 16 times of diluent. Thoroughly mix it up. Then, in accordance with Table 1,
inject mice.
5.4 Mouse Test
Select 6 healthy ICR strain of male mice, weight: 16 g ~ 20 g. Randomly divide them
into two groups, namely, test group and solvent control group; 3 mice in each group.
Enzyme Linked Immunosorbent Assay (ELISA
method)
7 Principle
In accordance with competitive enzyme-linked immunoreactivity, dissociative diarrheic
shellfish poison compete with its enzyme marker for diarrheic shellfish poison antibody.
Unbonded enzyme marker is eliminated in the step of rinsing. Add enzyme substrate
and color developing reagent to the hole and incubate it. The bonded enzyme marker
converts colorless color former into blue product. After adding reaction termination fluid,
the color turns from blue to yellow. Under the wavelength of 450 nm, use ELIASA to
measure the absorbance value of microporous solution. The content of diarrheic
shellfish poison in the sample is inversely proportional to the absorbance value. In
accordance with the standard curve being drawn, conduct quantitative calculation.
8 Reagents and Materials
Unless it is otherwise stipulated, all reagents used in this Method shall be analytically
pure. Water shall be Grade-1 water stipulated in GB/T 6682.
8.1 Reagents
8.1.1 Methanol (CH3OH).
8.1.2 Disodium hydrogen phosphate dodecahydrate (Na2HPO412H2O).
8.1.3 Sodium chloride (NaCl).
8.1.4 Potassium chloride (KCl).
8.1.5 Potassium dihydrogen phosphate (KH2PO4).
8.1.6 Tween-20 (C58H114O26).
8.1.7 Bovine serum albumin (BSA).
8.1.8 Enzyme marker.
8.1.9 Hydrogen peroxide (H2O2).
8.1.10 3,3,5,5-tetramethylbenzidine (TMB, C16H20N2).
8.1.11 Sulfuric acid (H2SO4).
8.2 Preparation of Reagents
10 Analytical procedures
10.1 Sample Collection
Same as 5.1.
10.2 Sample Preparation
Same as 5.2.
10.3 Sample Extraction
Homogenize the sample that is already cut into pieces. Accurately weigh-take 10 g
(accurate to 0.1 g) of the sample; add 50 mL of methanol solution (90%). Conduct
homogenization for 1 min ~ 2 min. At 6,000 r/min, conduct centrifugation for 10 min.
Transfer the supernatant. In accordance with the volume of the supernatant, add PBS
solution, which is twice the volume of the supernatant. Thoroughly mix it up. Absorb 50
μL of the sample diluent for determination.
10.4 Determination
Insert microporous strip, which is coated with diarrheic shellfish poison antibody, into
a microporous rack; leave a mark, which includes blank control hole, standard solution
hole and sample solution hole. Respectively make parallel holes. Add 50 μL of PBS
solution to the blank control hole; add 50 μL of diarrheic shellfish poison standard
series working solution to the standard solution hole; add 50 μL of sample solution to
the sample solution hole. Add 50 μL of diarrheic shellfish poison enzyme marker to
each microporous hole. Promptly and thoroughly mix it up. At 22 °C ~ 25 °C, keep
away from light, incubate for 10 min. After the incubation is completed, pour away the
liquid in the holes. Inject 250 μL of eluent to rinse each microporous hole. Overturn the
microporous board; pour away the liquid in the holes. Then, report the above-
mentioned board-rinsing operation for four times. On a water-absorbent paper, pat it
dry. Add 50 μL of hydrogen peroxide and TMB to each hole; thoroughly mix them up.
At room temperature, keep away from light, incubate for 6 min. Add 50 μL of sulfuric
acid solution (1 mol/L) to each hole; promptly and evenly mix them up. Then, terminate
the reaction. Within 10 min, under the wavelength of 450 nm, measure and record the
absorbance value.
If after the determination, the mass concentration of the extract exceeds the linear rage
of the standard curve, properly dilute it, then, re-determine it.
10.5 Draw a Standard Curve
Take the logarithm of diarrheic shellfish poison standard working solution (mass
concentration: 10 as the substrate) as the x-coordinate. Take the percent absorbance
value of the standard solution calculated through Formula (1) as the y-coordinate.
Liquid Chromatography - Tandem Mass Spectrometry
13 Principle
Use methanol to extract sample. Under alkaline condition, hydrolyze to release
esterified state of diarrheic shellfish poison. Use liquid chromatography for separation;
use tandem mass spectrometry for determination. Use the matrix standard curve to
quantify through external standard method.
14 Reagents and Materials
Unless it is otherwise stipulated, all reagents used in this Method shall be superior
grade of purity. Water shall be Grade-1 water stipulated in GB/T 6682.
14.1 Reagents
14.1.1 Methanol (CH3OH): chromatographic purity.
14.1.2 Acetonitrile (CH3CN): chromatographic purity.
14.1.3 Ammonia (NH3H2O).
14.1.4 Sodium hydroxide (NaOH).
14.1.5 Hydrochloric acid (HCl).
14.1.6 Ammonium formate (NH4COOH): chromatographic purity.
14.1.7 Formic acid (HCOOH): chromatographic purity.
14.2 Preparation of Reagents
14.2.1 Methanol solution (30%): measure-take 30 mL of methanol; use water to dilute
to 100 mL.
14.2.2 Methanol solution (20%): measure-take 20 mL of methanol; use water to dilute
to 100 mL.
14.2.3 Ammonia - methanol solution (0.3%): absorb 0.3 mL of ammonia; use methanol
to dilute to 100 mL.
14.2.4 Sodium hydroxide solution (2.5 mol/L): accurately weigh-take 50 g of sodium
hydroxide; use water to dissolve and dilute to 500 mL.
14.2.5 Hydrochloric acid solution (2.5 mol/L): accurately measure-take 104.5 mL of
hydrochloric acid; use water to dilute to 500 mL.
constant volume of 20 mL.
16.3.2 Hydrolysis release of esterified state of diarrheic shellfish poison
Accurately absorb 1 mL of the extract; place it in a threaded-mouth sample bottle. Add
125 μL of sodium hydroxide solution (2.5 mol/L); mix it up. Then, use sealing film to
seal up the bottle. At 76 °C, conduct incubation for 40 min. After cooling it down to
room temperature, add 125 μL of hydrochloric acid solution (2.5 mol/L), then, mix it up.
The obtained hydrolysate (1.25 mL is equivalent to 0.1 g of sample) may be directly
filtered through 0.22 μm organic phase microporous membrane, then, used for liquid
chromatography - tandem mass spectrometry determination. Or, if necessary,
purification treatment may also be conducted.
16.4 Sample Purification
Use 3 mL of water to dilute the obtained hydrolysate. After vortex mixing, transfer it
into previously-activated polymer solid phase extraction column. After the fluid flows
out at the flow rate of 1 mL/min, use 1 mL of methanol solution (20%) to rinse it. Discard
the effluent. Maintain pumping for 2 min. In the end, use 1 mL of ammonia - methanol
solution (0.3%) to elute it. Maintain pumping for 2 min; gather the eluent. Use methanol
to reach a constant volume of 1 mL (equivalent to 0.1 g of sample). Filter it through
0.22 μm organic phase microporous membrane; it may be used for liquid
chromatography - tandem mass spectrometry determination.
16.5 Blank Test
Except from the step of adding sample, adopt the same steps of operation as the
sample. Thus, obtain the blank solution.
16.6 Instrument Reference Conditions
16.6.1 Liquid chromatograph has the following reference conditions:
a) Chromatographic column: C18 column; column length: 100 mm; internal
diameter: 2.1 mm; particle size: 3.5 μm, or others with equivalent performance;
b) Flow rate: 0.2 mL/min;
c) Column temperature: 35 °C;
d) Injection volume: 10 mL;
e) Mobile phase: mobile phase A: ammonium formate solution (2 mmol/L); mobile
phase B: acetonitrile + ammonium formate (2 mmol/L) (95 + 5); gradient elution.
Please refer to Table 2 for the conditions of gradient elution.
......
GB/T 5009.212-2008
Determination of diarrhetic shellfish poison in shellfish
ICS 67.040
C53
National Standards of People's Republic of China
Determination of diarrheal shellfish Shellfish Toxin
Posted 2008-11-21
2009-03-01 implementation
People's Republic of China Ministry of Health
Standardization Administration of China released
Foreword
This revised standard adopts the Japanese Ministry milk ring No. 37 Notice "diarrhea shellfish toxin testing methods."
The main differences compared to the standard method with the Japanese Ministry of Health.
--- Added "normative references", "Terms and Definitions";
--- Added "instruments and equipment";
--- On the "Save and sample preparation", "reagents and materials" have been modified;
--- In the "result of the determination and the expression" standardized presentation of results.
This standard is proposed and administered by the People's Republic of China Ministry of Health.
This standard by the People's Republic of China Ministry of Health is responsible for interpretation.
This standard was drafted. People's Republic of China Liaoning Entry Inspection and Quarantine Bureau, People's Republic of China Yunnan Entry-Exit Inspection and
Quarantine Bureau.
The main drafters of this standard. Juan Cao occasion, Wangqiu Yan, Yu Jie, the soldiers, Huang Daliang, Sunzhe Ping, Song Huijun, Zheng Huifang, Ding, Xue Zhongliang,
Vega Xu Zheng Moon.
Determination of diarrheal shellfish Shellfish Toxin
1 Scope
This standard specifies the method for determination of shellfish and their products diarrheal shellfish toxins.
This standard applies to shellfish and their products - Determination of diarrheal shellfish toxins.
2 Normative references
The following documents contain provisions which, through reference in this standard and become the standard terms. For dated references, subsequent
Amendments (not including errata content) or revisions do not apply to this standard, however, encourage the parties to the agreement are based on research
Whether the latest versions of these documents. For undated reference documents, the latest versions apply to this standard.
GB/T 6682 analytical laboratory use specifications and test methods (GB/T 6682-2008, ISO 3696. 1987, MOD)
GB 14925 Laboratory Animal Facilities and Environment
3 Terms and Definitions
The following terms and definitions apply to this standard.
3.1
In okadaic acid (okadaicacid, OA) and its derivatives represented after ingestion can produce diarrhea as the main feature present in the
Shellfish marine life toxic substances in general.
3.2
Weighing 16g ~ 20g for the three each male ICR mice by intraperitoneal injection of 1mL shellfish toxin extract after making two or three small
The minimum amount of toxin in mice died within 24h defined as a mouse units.
Principle 4
Extracted with acetone DSP toxins in shellfish, after ethyl ether, evaporated to dryness under reduced pressure, and then to 1% Tween-60 saline dispersion
Media preparation DSP-1% Tween -60 saline suspension, the suspension was injected into the abdominal cavity of mice, survival was observed in mice, its calculated
Virulence.
5 Reagents and materials
Unless otherwise specified in this standard reagents were analytical grade water to comply with GB/T 6682 provided a water.
5.1 acetone (C3H6O).
5.2 dry ether (C4H10O).
5.31% Tween-60 NS. Weigh 1.0g Tween -60 (C64H126O26), dissolved in physiological saline (0.85% NaCl), and
Volume to 100.0mL.
6 instruments and equipment
6.1 rotary evaporator.
6.2 round-bottomed flask. 500mL, 250mL, 100mL, 50mL.
6.3 homogenizer.
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