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US$209.00 · In stock Delivery: <= 3 days. True-PDF full-copy in English will be manually translated and delivered via email. GB 29225-2012: National food safety standards -- Food additives -- Attapulgite clay Status: Valid
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National food safety standards -- Food additives -- Attapulgite clay
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GB 29225-2012
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Basic data | Standard ID | GB 29225-2012 (GB29225-2012) | | Description (Translated English) | National food safety standards -- Food additives -- Attapulgite clay | | Sector / Industry | National Standard | | Classification of Chinese Standard | X09 | | Word Count Estimation | 9,977 | | Regulation (derived from) | Ministry of Health Bulletin No. 23 of 2012 | | Issuing agency(ies) | Ministry of Health of the People's Republic of China | | Summary | This Chinese standard applies to attapulgite clay as raw material by acid activation, the production of food additives roasting process attapulgite clay. |
GB 29225-2012: National food safety standards -- Food additives -- Attapulgite clay---This is a DRAFT version for illustration, not a final translation. Full copy of true-PDF in English version (including equations, symbols, images, flow-chart, tables, and figures etc.) will be manually/carefully translated upon your order.
National food safety standards.Foodds.Attapulgite clay
National Standards of People's Republic of China
National standards for food safety
Food additives attapulgite clay
2012-12-25 release
2013-01-25 Implementation
Issued by the Ministry of Health of the People's Republic of China
National standards for food safety
Food additives attapulgite clay
1 Scope
This standard applies to the attapulgite clay as raw material using acid activation, roasting process production of food additives attapulgite clay.
2 molecular formula and relative molecular mass
2.1 Molecular formula
(Mg, Al) 2Si4O10 (OH) 4H2O
2.2 Relative molecular mass
463.85 (according to the.2007 International Relative Atomic Quality)
3 technical requirements
3.1 sensory requirements
Shall comply with the provisions of Table 1.
Table 1 sensory requirements
The project requires a test method
Color gray or light yellow
State powder
Take the appropriate amount of sample in a 50 mL beaker
Under the light to observe the color and state
3.2 Physical and chemical indicators
Shall comply with the provisions of Table 2.
Table 2 Physical and chemical indicators
Item Index Test Method
Decolorization rate,% ≥ 70 Appendix A, A.4
Moisture, w /% ≤ 10.0 Appendix A, A.5
Free acid (calculated as H2SO4), w /% ≤ 0.20 Appendix A A.6
Fineness (through 75 μm mesh), w /% ≥ 85 Appendix A A.7
Bulk density/(g/cm3) 0.5 to 1.0 Appendix A A.8
Heavy metals (Pb)/(mg/kg) ≤ 40 GB/T 5009.74
Total arsenic (in As)/(mg/kg) ≤ 3 GB/T 5009.76
Appendix A
Testing method
A.1 Warning
Some of the reagents used in the test methods of this standard are toxic or corrosive and require careful operation such as splashing on the skin
That is, rinse with water, severe cases should be treated immediately.
A.2 General provisions
Unless otherwise stated, only the reagents identified as analytical reagents and the tertiary water specified in GB/T 6682-2008 are used in the analysis. test
Method used in the standard titration solution, impurity determination standard solution, preparation and products, without any other requirements, according to GB/T 601,
GB/T 602 and GB/T 603; the solution used in the absence of specified solvent, refers to the aqueous solution.
A.3 Identification test
A.3.1 X-ray diffraction spectroscopy identification
The X-ray diffraction spectrum of attapulgite clay should be consistent with Figure B.1 in Appendix B.
A.3.2 Magnesium oxide (MgO) content test
The mass fraction of magnesium oxide measured by X-ray fluorescence spectrometer should not be less than 6%.
A.4 Determination of decolorization rate
A.4.1 Methodological Summary
Take a certain amount of neutralized soybean oil, add a certain quality of the sample for decolorization, measured decolorization after the oil absorbance. According to the absorbance
Decrease the value to calculate the decolorization rate as a percentage.
A.4.2 Reagents and materials
A.4.2.1 Soybean oil. clarifies fresh and neutralized soybean oil with an absorbance between 0.2 and 0.4.
A.4.2.2 Medium speed qualitative filter paper.
A.4.3 Instruments and equipment
A.4.3.1 Spectrophotometer. with 1cm cuvette.
A.4.3.2 Constant temperature magnetic stirrer.
A.4.4 Analysis steps
Weighed 0.4000 g of the sample which had been dried at 105 ° C ± 3 ° C and placed in a 50 mL dry grinding flask and added with soybean oil
40.00g, the oil into the thermometer and sealed with a casing, it will be placed on the preheated constant temperature magnetic stirrer, while heating and stirring, heating
Time control in about 10min. The strength of the agitation is preferably in the form of a swirling motion of the entire oil sample. Keep the thermometer always submerged in the oil sample.
The temperature was raised to 110 ° C, and the temperature was maintained at 115 ° C ± 5 ° C and stirred for 25 min. After decolorization, take advantage of the double layer
Quick-quality filter paper filter in 50mL dry beaker. The above-mentioned clarified oil samples were measured on a spectrophotometer at a wavelength of 520 nm
The absorbance of the oil sample (with 1cm cuvette, water for reference, calibration zero). Simultaneous determination of non-decolorized soy and neutralized oil at 520 nm
The absorbance at the wavelength.
A.4.5 Calculation of results
The decolorization rate X1 is calculated according to formula (A.1)
X1 =
A0-A1
A0 × 100%
(A.1)
Where.
A0 --- non-decolorized oil samples at 520nm wavelength absorbance.
A1 - the absorbance of the decolored oil sample at the wavelength of 520 nm.
The experimental results are based on the arithmetic mean of the parallel measurement results, and the absolute difference between the two parallel measurements is not more than 2%.
A.5 Determination of moisture
Determination of moisture by GB 5009.3 direct drying method, the drying temperature of 105 ℃ ± 3 ℃.
A.6 Determination of free acid (measured in H2SO4)
A.6.1 Methodological summary
The free acid in the sample was leached with water and titrated with sodium hydroxide as the indicator. The titration of the sample was calculated by titration.
Acid content.
A.6.2 Reagents and materials
A.6.2.1 Sodium hydroxide standard titration solution. c (NaOH) = 0.02 mol/L.
A.6.2.2 phenolphthalein indicator solution. Weigh 0.1g phenolphthalein (C20H14O4), dissolved in 100mL anhydrous ethanol.
A.6.2.3 Medium speed qualitative filter paper.
A.6.3 Analysis steps
Weigh the sample about 1g, accurate to 0.0001g, placed in a 150mL beaker, add 50mL of water, boil for 3min. Filter on
250mL Erlenmeyer flask, wash the beaker with hot water and filter paper 4 to 5 times (total water consumption of about 50mL), covered with caustic soda asbestos drying tube glue
Plug, cool to room temperature. Remove the rubber stopper, wash the cone wall with water, add 2 to 3 drops of phenolphthalein indicator solution, immediately with sodium hydroxide standard titration solution
Liquid titration to reddish and keep for 30s without fading as the end. At the same time as a blank experiment.
A.6.4 Calculation of results
The mass fraction w1 of the free acid (calculated as H2SO4) is calculated according to formula (A.2)
w1 =
[(V-V0)/1000] × c × M
m x 100%
(A.2)
Where.
V - titration sample solution consumes the volume of sodium hydroxide standard titration solution in milliliters (mL);
V0 --- titration blank solution consumes the volume of sodium hydroxide standard titration solution in milliliters (mL);
c - the concentration of sodium hydroxide standard solution in moles per liter (mol/L);
M - sulfuric acid (1/2H2SO4) molar mass in grams per mole (g/mol) (M = 49.04);
m --- sample quality, in grams (g);
1000 --- conversion factor.
The experimental results are based on the arithmetic mean of the parallel measurement results, and the absolute difference between the two measurements is not more than 0.04%.
A.7 Determination of fineness
A.7.1 Methodological Summary
Take a certain amount of the sample in a standard sieve of 75μm sieve, dry sieve, the screen sieve residue weighing, calculated through the screen of the hundred
fraction.
A.7.2 Instruments and equipment
A.7.2.1 Standard sieve. 75μm sieve, in line with GB/T 6003.1 requirements.
A.7.2.2 plate 6 brush.
A.7.3 Analysis steps
Weigh the sample about 20g, accurate to 0.0001g, placed in a standard sieve, with a brush on the 6th brush gently brush until the sieve sample brush no less
Only, the quality of the sieve residue is measured, accurate to 0.0001g.
A.7.4 Calculation of results
The fineness (through the 75 μm mesh) w2 is calculated as the mass fraction, according to formula (A.3)
w2 =
m-m1
m x 100%
(A.3)
Where.
m --- the quality of the sample, in grams (g);
m1 --- did not pass the quality of the standard sieve sample, in grams (g).
The experimental results are based on the arithmetic mean of the parallel measurement results, and the absolute difference between the two parallel measurements is not more than 2%.
A.8 Determination of bulk density
A.8.1 Methodological Summary
The sample was placed in a funnel of a bulk density measuring device and allowed to fall into a known volume of the tank and then measured in a loose bulk
The mass of the unit sample volume.
A.8.2 Instruments and equipment
Bulk density measurement device shown in Figure A.1, tank volume is known, the volume measurement method see Appendix C.
1 --- material tank;
2 - stent;
3 --- funnel.
Figure A.1 Bulk density measuring device
A.8.3 Analysis steps
A.8.3.1 Install the bulk density measuring device as shown in Figure A.1.
A.8.3.2 Weigh the quality of the tank, accurate to 0.1g.
A.8.3.3 Close the bottom of the funnel, the specimen is completely filled, with a straight ruler to scratch the higher part. Place the known mass of the tank under the funnel
At the end, so that all the sample into the tank (can be stuck with a glass rod), with a straight ruler to scratch the higher part (scraping before not moving the tank), weighing the sample and
The quality of the tank is accurate to 0.1g.
A.8.4 Calculation of results
The bulk density X2 is expressed in grams per cubic centimeter (g/cm3) and is calculated according to formula (A.4)
X2 =
m3-m4
(A.4)
Where.
m3 --- the quality of the tank and the sample, in grams (g);
m4 --- the quality of the tank, in grams (g);
V --- the volume of the tank, in cubic centimeters (cm3).
The experimental results are based on the arithmetic mean of the parallel measurement results, and the absolute difference between the two parallel measurements is not more than 0.02 g/cm3.
Appendix B
X - ray Diffraction Spectra of Attapulgite Clay of Food Additive
X-ray diffraction spectra of the food additive attapulgite clay see B.1.
Figure B.1 X-ray diffraction spectra of Cu (superscript 2 +) -
Appendix C.
Determination of tank volume
C.1 Analysis steps
Wash the jars, dry, cover the glass, weighing the quality of the tank and glass, accurate to 0.1g. Be careful to pour the water into the tank
When the use of dropper to full, covered with glass, with filter paper suction tank and glass outside the water, glass and the water between the tank should be no gas
bubble. And then weighing the quality of the tank and glass, accurate to 0.1g.
C.2 Calculation of results
The volume V of the tank is expressed in cubic centimeters (cm3) and calculated as (C.1)
V =
m1-m2
ρ0
(C.1)
Where.
m1 --- the quality of the tank and glass filled with water, in grams (g);
m2 --- the quality of the tank and glass sheet without irrigation, in grams (g);
ρ0 --- Determine the density of water at the temperature in grams per cubic centimeter (g/cm3).
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