GB 15892-2020_English: PDF (GB15892-2020)
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Polyaluminium chloride for treatment of drinking water
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GB 15892-2020
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| GB 15892-2009 | English | 719 |
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Poly aluminium chloride for treatment of drinking water
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GB 15892-2009
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| GB 15892-2003 | English | 679 |
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Water treatment chemical -- Poly aluminium chloride
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GB 15892-2003
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| GB 15892-1995 | English | 639 |
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Water treatment chemicals--Poly aluminium chloride
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GB 15892-1995
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| Standard ID | GB 15892-2020 (GB15892-2020) | | Description (Translated English) | Polyaluminium chloride for treatment of drinking water | | Sector / Industry | National Standard | | Classification of Chinese Standard | G77 | | Classification of International Standard | 71.100.80 | | Word Count Estimation | 22,293 | | Date of Issue | 2020-07-23 | | Date of Implementation | 2021-08-01 | | Older Standard (superseded by this standard) | GB 15892-2009 | | Administrative Organization | Ministry of Industry and Information Technology of the People's Republic of China | | Proposing organization | Ministry of Industry and Information Technology of the People's Republic of China | | Issuing agency(ies) | State Administration for Market Regulation, National Standardization Administration | | Standard ID | GB 15892-2009 (GB 15892-2009) | | Sector / Industry | National Standard | | Classification of Chinese Standard | G77 | | Classification of International Standard | 71.100.80 | | Word Count Estimation | 18,131 | | Date of Issue | 2009-04-08 | | Date of Implementation | 2009-09-01 | | Older Standard (superseded by this standard) | GB 15892-2003 | | Quoted Standard | GB/T 191; GB/T 601; GB/T 602; GB/T 603; GB/T 610; GB/T 6678; GB/T 6682; GB/T 8946 | | Drafting Organization | Run water Shenzhen Industrial Technology Development Co., Ltd. | | Administrative Organization | National Standardization Technical Committee of Water Treatment Chemicals Branch | | Regulation (derived from) | Announcement of Newly Approved National Standards No. 3, 2009 (No. 143 overall) | | Proposing organization | China Petroleum and Chemical Industry Association | | Issuing agency(ies) | Administration of Quality Supervision, Inspection and Quarantine of People's Republic of China; Standardization Administration of China | | Summary | This Chinese standard provides drinking water using poly aluminum chloride requirements, test methods, inspection rules, packaging, labeling, transportation and storage. This standard applies to drinking water using poly aluminum chloride. The product is mainly used for drinking water purification. Raw material for the production of poly aluminum chloride, hydrochloric acid, hydrochloric acid should be used industrial synthesis, aluminum raw materials should be used in industrial aluminum hydroxide, kaolin, a boehmite, gibbsite and water treatment agent aluminum calcium. Exemplary formula: Aln? (OH) mCl (3n-m) 0 < m < 3n | | Standard ID | GB 15892-2003 (GB15892-2003) | | Description (Translated English) | Water treatment chemical--Poly aluminium chloride | | Sector / Industry | National Standard | | Classification of Chinese Standard | G77 | | Classification of International Standard | 71.100.80 | | Word Count Estimation | 17,113 | | Date of Issue | 2003/6/13 | | Date of Implementation | 2003/12/1 | | Older Standard (superseded by this standard) | GB 15892-1995 | | Quoted Standard | GB/T 191-2000; GB/T 601-2002; GB/T 602-2002; GB/T 603-2002; GB/T 610.1-1988; GB/T 610.2-1988; GB/T 6678-1986; GB/T 6682-1992 | | Adopted Standard | JIS K1475-1996, NEQ; ANSI/AWWA B408-1993, NEQ | | Regulation (derived from) | Announcement of Newly Approved National Standards 2009 No. (No. 143 overall) 3 | | Proposing organization | The former National Petroleum and Chemical Industry Bureau | | Issuing agency(ies) | General Administration of Quality Supervision, Inspection and Quarantine of the People Republic of China |
GB 15892-2020
GB
NATIONAL STANDARD OF THE
PEOPLE’S REPUBLIC OF CHINA
ICS 71.100.80
G 77
Replacing GB 15892-2009
Polyaluminium chloride for treatment of drinking
water
ISSUED ON: JULY 23, 2020
IMPLEMENTED ON: AUGUST 01, 2021
Issued by: State Administration for Market Regulation;
Standardization Administration of the PRC.
Table of Contents
Foreword ... 3
1 Scope ... 4
2 Normative references ... 4
3 Molecular formula ... 5
4 Product classification ... 5
5 Requirements ... 5
5.1 Raw material requirements ... 5
5.2 Technical requirements ... 5
6 Test methods ... 6
6.1 General ... 6
6.2 Determination of alumina (Al2O3) content ... 6
6.3 Determination of basicity ... 12
6.4 Determination of density ... 13
6.5 Determination of insoluble matter content ... 14
6.6 Determination of pH value ... 15
6.7 Determination of iron content ... 15
6.8 Determination of arsenic content ... 15
6.9 Determination of lead content ... 20
6.10 Determination of cadmium content ... 24
6.11 Determination of mercury content ... 27
6.12 Determination of chromium content ... 32
7 Inspection rules ... 33
8 Marking, packaging, transportation and storage ... 34
Appendix A (Informative) Determination of coagulation performance ... 36
Polyaluminium chloride for treatment of drinking
water
Warning - The strong acids and bases used in this Standard are corrosive.
During use, it shall avoid inhalation or contact with the skin. If splashed
on the body, it shall rinse immediately with plenty of water; in severe
cases, it shall seek medical attention immediately.
1 Scope
This Standard specifies the requirements, test methods, inspection rules,
marking, packaging, transportation and storage of polyaluminium chloride for
treatment of drinking water.
This Standard applies to polyaluminium chloride for treatment of drinking water.
The product is mainly used for the purification of drinking water.
2 Normative references
The following documents are indispensable for the application of this document.
For the dated references, only the editions with the dates indicated are
applicable to this document. For the undated references, the latest edition
(including all the amendments) are applicable to this document.
GB/T 191 Packaging - Pictorial marking for handling of goods
GB/T 320 Synthetic hydrochloric acid for industrial use
GB/T 601 Chemical reagent - Preparations of reference titration solutions
GB/T 602 Chemical reagent - Preparations of standard solutions for impurity
GB/T 603 Chemical reagent - Preparations of reagent solutions for use in
test methods
GB/T 610-2008 Chemical reagent - General method for the determination of
arsenic
GB/T 4294 Aluminium hydroxide
GB/T 6678 General principles for sampling chemical products
the excess EDTA solution, to get alumina (Al2O3) content.
6.2.1.2 Reagents and materials
6.2.1.2.1 Carbon dioxide-free water.
6.2.1.2.2 Nitric acid solution: 1+12.
6.2.1.2.3 Aqueous ammonia solution: 1+1.
6.2.1.2.4 Disodium ethylenediaminetetraacetic acid (EDTA) solution: c(EDTA)
is about 0.05 mol/L.
6.2.1.2.5 Acetic acid-sodium acetate buffer solution (pH=5.5): WEIGH 272 g of
sodium acetate (trihydrate) and dissolve it in water; ADD 19 mL of glacial acetic
acid; and dilute to 1000 mL.
6.2.1.2.6 Alumina standard solution: 1 mL contains 0.001 g of Al2O3. WEIGH
0.5293 g of high-purity aluminium (≥99.99%), accurate to 0.2 mg. PLACE it in
a 200 mL polyethylene cup; ADD 20 mL of water; ADD about 3 g of sodium
hydroxide, to make it all dissolved and transparent (if necessary, heat on a
water bath). USE hydrochloric acid solution (1+1) to adjust to acidic and then
add 10 mL, to make it transparent, cool; TRANSFER to a 1000 mL volumetric
flask; DILUTE to the mark and shake well.
6.2.1.2.7 Zinc chloride reference titration solution: c(ZnCl2) is about 0.025 mol/L;
prepare as follows:
a) Preparation: WEIGH 3.5 g of zinc chloride (ZnCl2); DISSOLVE it in
hydrochloric acid solution [0.05% (volume fraction)]; DILUTE to 1 L and
shake well.
b) Calibration: PIPETTE 20 mL of EDTA solution and 40 mL of alumina
standard solution; PUT them in a 250 mL conical flask; follow the steps in
6.2.1.3 "ADD 10 mL of nitric acid solution..." to start the operation. READ
the consumption V (mL) of the zinc chloride reference titration solution. In
addition, pipette 20 mL of EDTA solution and place it in a 250 mL conical
flask. Follow the steps in 6.2.1.3 "ADD 10 mL of nitric acid solution..." to
start the operation. READ the consumption V0 (mL) of the zinc chloride
reference titration solution.
c) Result calculation: The concentration of zinc chloride reference titration
solution, c(ZnCl2), value expressed in moles per liter (mol/L), is calculated
according to formula (1):
Where:
V0 - The value of the volume of sodium hydroxide reference titration solution
consumed in the blank test, in milliliters (mL);
V - The value of the volume of sodium hydroxide reference titration solution
consumed for determination of the sample, in milliliters (mL);
c - The exact value of the actual concentration of sodium hydroxide reference
titration solution, in moles per liter (mol/L);
M - The value of the molar mass of hydroxide (OH-), in grams per mole (g/mol)
(M=16.99);
m - The value of the mass of the test portion, in grams (g);
w1 - The mass fraction of alumina measured in 6.2;
V1 - The value of the volume of test solution A pipetted, in milliliters (mL) (V1=25);
VA - The value of the total volume of test solution A, in milliliters (mL) (VA=250);
M1 - The value of the molar mass of aluminium, in grams per mole (g/mol)
(M1=26.98);
M2 - The value of the molar mass of alumina, in grams per mole (g/mol)
(M2=101.96).
6.3.5 Allowable difference
USE the arithmetic mean of the parallel determination results as the
determination result. The absolute difference of the parallel determination
results is not more than 2.0%.
6.4 Determination of density
6.4.1 Method summary
From the depth of immersion when the densitometer reaches the equilibrium
state in the measured liquid, read the density value.
6.4.2 Apparatus
6.4.2.1 Densitometer: The division value is 0.001 g/cm3.
6.4.2.2 Constant-temperature water bath: Controllable temperature (20±0.1)°C.
6.4.2.3 Thermometer: The division value is 0.1 °C.
standard solution respectively in five 100 mL volumetric flasks. Respectively
add 5.0 mL of hydrochloric acid and 20 mL of thiourea solution; USE water to
dilute to the mark and shake well; PLACE for more than 30 min. The mass
concentrations of arsenic in this series of solutions are 0 μg/L, 4 μg/L, 8 μg/L,
12 μg/L, 16 μg/L, respectively.
6.8.1.4.2 After the instrument is stable, use potassium borohydride-sodium
hydroxide solution as the reducing agent; USE hydrochloric acid solution as the
carrier solution; under the best working conditions of the instrument, measure
its fluorescence value. USE the measured fluorescence value as the ordinate;
USE the corresponding mass concentration of arsenic (μg/L) as the abscissa,
to draw a calibration curve and calculate the regression equation.
Note: When using an atomic fluorescence spectrometer for determination, the required
potassium borohydride solution concentration, carrier solution concentration, linear
range of calibration curves of various elements, pH value of sample solution, etc. will
vary depending on the model of the instrument. Users can, according to the
instrument model, choose the best test conditions.
6.8.1.5 Analytical procedure
6.8.1.5.1 Pre-cleaning of glassware
The glassware used in the test shall, before use, be soaked in nitric acid
solution (1+4) for 24 h; then rinsed with water for later use.
6.8.1.5.2 Sample determination
WEIGH about 1.5 g of liquid sample or 0.5 g of solid sample, accurate to 0.2
mg; PLACE it in a 100 mL beaker. ADD 30 mL of water, 1 mL of nitric acid
solution (1+1); COVER with a watch glass and boil for about 1 min. After cooling
to room temperature, transfer to a 100 mL volumetric flask; respectively add 5.0
mL of hydrochloric acid, 20 mL of thiourea solution; USE water to dilute to the
mark and shake well. Perform the determination according to the steps of
6.8.1.4.2 (if there is turbidity, use a medium-speed quantitative filter paper to
dry-filter before the determination). The arsenic content is obtained from the
calibration curve or regression equation.
6.8.1.6 Result calculation
The arsenic content is calculated as the mass fraction w4. The value is
expressed in %, calculated according to formula (7):
arsenic standard stock solution in a 100 mL volumetric flask; USE water to dilute
to the mark and mix well. Before use, pipette 10.00 mL of this solution into a
100 mL volumetric flask; USE water to dilute to the mark and mix well.
6.8.2.2.9 Lead acetate cotton.
6.8.2.3 Apparatus
6.8.2.3.1 Spectrophotometer: With a 1 cm absorption cell.
6.8.2.3.2 Arsenic detector: Comply with the provisions of 4.2.2.3 in GB/T 610-
2008.
6.8.2.4 Analytical procedure
6.8.2.4.1 Drawing of calibration curve
6.8.2.4.1.1 In 6 dry arsenic determination bottles, add 0.00 mL, 1.00 mL, 2.00
mL, 3.00 mL, 4.00 mL, 5.00 mL of arsenic standard solution in sequence; and
then add 30 mL, 29 mL, 28 mL, 27 mL, 26 mL, 25 mL of water in sequence; to
make the total volume of the solution be 30 mL.
6.8.2.4.1.2 ADD 20 mL of stannous chloride hydrochloric acid solution, 5 mL of
potassium iodide solution, and 1 mL of copper sulfate solution to each arsenic
determination bottle; SHAKE well. At this time, the acidity c (in terms of H+) in
the solution shall be between 1.8 mol/L and 2.6 mol/L. PLACE in a dark place
for 30 min~40 min; ADD 5 g of arsenic-free zinc granules to the arsenic
determination bottle. Immediately install the absorption tube, filled with lead
acetate cotton and containing 5.0 mL of silver diethyldithiocarbamate-
triethylamine trichloromethane solution (absorption liquid), on the arsenic
determination bottle; react for 25 min~35 min (Avoid direct sunlight. If the
absorption liquid volatilizes too fast, it shall pay attention to add
trichloromethane). TAKE off the absorption tube (do not suck the absorption
liquid backwards); USE trichloromethane to replenish the absorption liquid to
5.0 mL and mix well.
6.8.2.4.1.3 At a wavelength of 510 nm, use a 1 cm absorption cell; USE the
reagent blank as a reference; determine the absorbance.
6.8.2.4.1.4 USE the mass (mg) of arsenic as the abscissa; USE the
corresponding absorbance as the ordinate; DRAW a calibration curve, or
calculate a regression equation.
6.8.2.4.2 Determination
WEIGH about 10 g of liquid sample or 3.3 g of solid sample, accurate to 0.2 mg;
6.9.1.2 Reagents and materials
6.9.1.2.1 Nitric acid solution: 1+1.
6.9.1.2.2 Lead standard stock solution: 0.1 mg/mL.
6.9.1.2.3 Lead standard solution: PIPETTE 10.00 mL of lead standard stock
solution into a 1000 mL volumetric flask; ADD 20 mL of nitric acid solution; USE
water to dilute to the mark and shake well. 1 mL of this solution contains 1 μg
of Pb.
6.9.1.3 Apparatus
6.9.1.3.1 Micro-liquid feeding device: Equipped with a button type 5 μL~500 μL
micro-liquid flowmeter or automatic sampler.
6.9.1.3.2 Electric heating atomic absorption analysis device: Electric heating
method. Reverse grounding compensation can be carried out.
6.9.1.3.3 Heating furnace: Made of graphite or high-temperature-resistant metal.
6.9.1.3.4 Lead hollow cathode lamp.
6.9.1.4 Analytical procedure
6.9.1.4.1 WEIGH about 10 g of liquid sample or 3.3 g of solid sample, accurate
to 0.2 mg. PLACE it in a 250 mL beaker; ADD 30 mL of water and 10 mL of
nitric acid solution. COVER with a watch glass and boil for 1 min. After cooling
to room temperature, transfer to a 250 mL volumetric flask; USE water to dilute
to the mark and shake well. This solution is test solution C.
6.9.1.4.2 Respectively pipette 0.00 mL (blank), 1.00 mL, 2.00 mL, 3.00 mL of
lead standard solution into four 50 mL volumetric flasks. ADD 1 mL of nitric acid
solution; USE water to dilute to the mark and shake well. USE a micro-liquid
feeding device to inject the prepared sample into the heating furnace; after
drying, ashing and atomization, measure the absorbance at 283.3 nm. USE the
mass concentration (μg/L) of lead standard solution as the abscissa; USE the
corresponding absorbance as the ordinate; DRAW the calibration curve and
calculate the regression equation.
6.9.1.4.3 PIPETTE an appropriate volume of test solution C; operate according
to 6.9.1.4.2, and determine. The mass concentration of lead is obtained from
the calibration curve or regression equation.
6.9.1.5 Result calculation
The lead content is calculated as the mass fraction w5. The value is expressed
6.9.2.2.7 Sodium diethyldithiocarbamate solution: 100 g/L.
6.9.2.2.8 Lead standard stock solution: 1 mL contains 0.1 mg of Pb.
6.9.2.2.9 Lead standard solution: PIPETTE 10.00 mL of lead standard stock
solution into a 100 mL volumetric flask; ADD 15 mL of nitric acid solution; USE
water to dilute to the mark and shake well. 1 mL of this solution contains 0.01
mg of Pb.
6.9.2.3 Apparatus
6.9.2.3.1 Atomic absorption spectrometer.
6.9.2.3.2 Lead hollow cathode lamp.
6.9.2.4 Analytical procedure
6.9.2.4.1 WEIGH about 5 g of liquid sample or 1.5 g of solid sample, accurate
to 0.2 mg. PLACE it in a 250 mL beaker; ADD 30 mL of water, 2 mL of nitric acid
solution; COVER with a watch glass and boil for about 1 min; and cool to room
temperature.
6.9.2.4.2 ADD 3 mL of ammonium citrate solution and 15 mL of ammonium
sulfate solution; USE aqueous ammonia solution or hydrochloric acid solution,
to adjust the pH value to 5.0~5.2 (use a pH meter). Then, respectively add 3
mL of sodium diethyldithiocarbamate solution and mix well.
6.9.2.4.3 After standing for 3 min, transfer to the separatory funnel.
Successively add 25.00 mL of 4-methyl-2-pentanone; MIX for 2 min. After
standing for another 10 min, discard the aqueous layer; COLLECT the extract
in a dry volumetric flask.
6.9.2.4.4 Under the best working conditions of the instrument, at a wavelength
of 283.3 nm, use the reagent blank for zero setting; determine the absorbance.
6.9.2.4.5 Respectively pipette 0.00 mL (blank), 2.5 mL, 5.00 mL, 7.5 mL of lead
standard solution into 100 mL beakers; ADD water to about 30 mL. Follow the
steps of 6.9.2.4.2~6.9.2.4.4. USE the measured absorbance as the ordinate;
USE the corresponding lead mass (mg) as the abscissa; DRAW the calibration
curve and calculate the regression equation.
6.9.2.5 Result calculation
The lead content is calculated as the mass fraction w5. The value is expressed
in %, calculated according to formula (10):
mercury in the sample is reduced by potassium borohydride (KBH4) to atomic
mercury, which is brought by the carrier gas (argon) into the atomizer. Under
the irradiation of a special mercury hollow cathode lamp, the ground state
mercury atoms are excited to the upper state. When deactivated to the ground
state, they emit fluorescence with a characteristic wavelength. Its fluorescence
intensity is proportional to the mercury content. Quantitatively compare with the
standard series.
6.11.1.2 Reagents and materials
6.11.1.2.1 Nitric acid: Guaranteed reagent.
6.11.1.2.2 Hydrochloric acid: Guaranteed reagent.
6.11.1.2.3 Nitric acid solution: 1+1.
6.11.1.2.4 Nitric acid solution: (1+4)
6.11.1.2.5 Hydrochloric acid solution: 1+19.
6.11.1.2.6 Potassium borohydride-sodium hydroxide solution: WEIGH 2.5 g of
sodium hydroxide and 10.0 g of potassium borohydride in a polyethylene
beaker; USE water to dissolve and dilute to 1000 mL. Prepare this solution at
the time of use.
6.11.1.2.7 Mercury standard stock solution: 0.1 mg/mL.
6.11.1.2.8 Mercury standard solution (I): 5 μg/mL. PIPETTE 5 mL of mercury
standard stock solution in a 100 mL volumetric flask; ADD 0.05 g of potassium
dichromate, 5 mL of nitric acid; USE water to dilute to the mark. Prepare this
solution at the time of use.
6.11.1.2.9 Mercury standard solution (II): 0.05 μg/mL. PIPETTE 1 mL of
mercury standard solution (I) into a 100 mL volumetric flask; ADD 0.05 g of
potassium dichromate, 5 mL of hydrochloric acid; USE water to dilute to the
mark. Prepare this solution at the time of use.
6.11.1.3 Apparatus
6.11.1.3.1 Atomic fluorescence spectrophotometer.
6.11.1.3.2 Mercury hollow cathode lamp.
6.11.1.4 Drawing of calibration curve
6.11.1.4.1 Respectively take 0.00 mL (blank), 2.00 mL, 4.00 mL, 6.00 mL, 8.00
mL, 10.00 mL of mercury standard solution (II) into six 100 mL volumetric flasks.
(V=100);
m - The value of the mass of the test portion, in grams (g).
6.11.1.7 Allowable difference
USE the arithmetic mean of the parallel determination results as the
determination result. The absolute difference of the parallel determination
results is not more than 0.000005%.
6.11.2 Cold atomic absorption method
6.11.2.1 Method summary
In an acid medium, oxidize the mercury in the sample to divalent mercury ions;
USE stannous chloride to reduce the mercury ions to mercury atoms; USE cold
atomic absorption method to determine mercury.
6.11.2.2 Reagents and materials
6.11.2.2.1 Sulfuric acid-nitric acid mixture: Slowly add 200 mL of sulfuric acid
(guaranteed reagent) to 300 mL of water, while stirring continuously. After
cooling, add 100 mL of nitric acid and mix well.
6.11.2.2.2 Sulfuric acid (guaranteed reagent) solution: 1+71.
6.11.2.2.3 Hydrochloric acid (guaranteed reagent) solution: 1+11.
6.11.2.2.4 Potassium permanganate (guaranteed reagent) solution: 10 g/L.
6.11.2.2.5 Hydroxylamine hydrochloride solution: 100 g/L.
6.11.2.2.6 Stannous chloride solution: 50 g/L. WEIGH 5.0 g of stannous
chloride; PLACE it in a 200 mL beaker. ADD 10 mL of hydrochloric acid solution
and an appropriate amount of water to dissolve it; DILUTE to 100 mL and mix
well.
6.11.2.2.7 Mercury standard stock solution: 1 mL of the solution contains 0.1
mg of Hg.
6.11.2.2.8 Mercury standard solution: 1 mL contains 0.001 mg of Hg.
6.11.2.3 Apparatus
6.11.2.3.1 Atomic absorption spectrophotometer or mercury vapor meter.
6.11.2.3.2 Mercury hollow cathode lamp.
6.11.2.6 Allowable difference
USE the arithmetic mean of the parallel determination results as the
determination result. The absolute difference of the parallel determination
results is not more than 0.000005%.
6.12 Determination of chromium content
6.12.1 Method summary
At a wavelength of 429.0 nm, use electrically heated atomic absorption
spectrometry to measure the absorbance of chromium atoms, to obtain the
chromium content.
6.12.2 Reagents and materials
6.12.2.1 Nitric acid solution: 1+1.
6.12.2.2 Chromium standard stock solution: 0.1 mg/mL.
6.12.2.3 Chromium standard solution: PIPETTE 10.00 mL of chromium
standard stock solution in a 1000 mL volumetric flask; ADD 20 mL of nitric acid
solution; USE water to dilute to the mark and shake well. 1 mL of this solution
contains 1 μg of Cr.
6.12.3 Apparatus
6.12.3.1 Micro-liquid feeding device: Equipped with a button type 5 μL~500 μL
micro-liquid flowmeter or automatic sampler.
6.12.3.2 Electric heating atomic absorption analysis device: Electric heating
method. Reverse grounding compensation can be carried out.
6.12.3.3 Heating furnace: Made of graphite or high-temperature-resistant metal.
Atomic absorption spectrophotometer.
6.12.3.4 Chromium hollow cathode lamp.
6.12.4 Analytical procedure
6.12.4.1 Respectively pipette 0.00 mL (blank), 1.00 mL, 2.00 mL, 3.00 mL of
chromium standard solution into four 50 mL volumetric flasks; ADD 1 mL of nitric
acid solution; USE water to dilute to the mark and shake well. USE a micro-
liquid feeding device to inject the prepared sample into the heating furnace;
after drying, ashing and atomization, measure the absorbance at 429.0 nm.
USE the mass concentration (μg/L) of chromium standard solution as the
abscissa; USE the corresponding absorbance as the ordinate; DRAW the
polyaluminium chloride, see Appendix A.
7.3 Each lot of products shall not exceed 200 t for liquid; and shall not exceed
60 t for solid.
7.4 According to GB/T 6678, determine the number of sampling units.
7.5 When sampling liquid products, the sampler shall be deep into the barrel.
The sampling volume from the upper, middle and lower parts shall not be less
than 100 mL. MIX the sampled product well; TAKE out about 800 mL from it;
DIVIDE it into two clean and dry glass bottles, and seal.
7.6 When sampling liquid products shipped in storage tanks, samplers shall be
used to sample from the upper, middle, and lower parts of the tank. The
sampling volume of each part is not less than 250 mL. MIX the sampled product
well; TAKE out about 800 mL from it; DIVIDE it into two clean and dry glass
bottles, and seal.
7.7 When sampling solid products, the sampler shall be inserted vertically into
three-quarters of the depth of the bag for sampling. The sample taken from
each bag shall not be less than 100 g. MIX the sampled product evenly; reduce
it to about 500 g using the quartering method; DIVIDE it into two clean and dry
glass bottles, and seal.
7.8 STICK a label on the sealed sample bottle, indicating the name of the
manufacturer, product name, lot number, sampling date, and the name of the
sampler. One bottle is for inspection; the other bottle is kept for 3 months for
future reference.
7.9 Determine according to the comparison method of rounded value in GB/T
8170.
7.10 If there is one index in the inspection results that does not meet the
requirements of this Standard, it shall re-sample from twice the number of
packaging units for verification. If there is still one item in the verification results
that does not meet the requirements of this Standard, the entire lot of products
is nonconformity.
8 Marking, packaging, transportation and storage
8.1 The outer packaging of polyaluminium chloride shall have a firm and clear
mark; which indicates the name of the manufacturer, product name, trademark,
net mass, lot number, production date, standard number, and the "avoid rain"
marking specified in GB/T 191.
......
GB 15892-2009
Poly aluminium chloride for treatment of drinking water
ICS 71.100.80
G77
National Standards of People's Republic of China
Replacing GB 15892-2003
Drinking poly aluminum chloride
Posted 2009-04-08
2009-09-01 implementation
Administration of Quality Supervision, Inspection and Quarantine of People's Republic of China
Standardization Administration of China released
Foreword
Table 1 of this standard product indicators are mandatory, other content are recommended.
This corresponds to the standard Japanese Industrial Standards JISK1475.2006 "Water poly aluminum chloride" (Japanese version) and the American Water Works Association Standard
Quasi ANSI/AWWAB408.2003 "liquid polyethylene aluminum chloride" (in English), and JISK1475.2006, ANSI/AWWAB408.
2003 non-equivalent degree of consistency.
This standard JISK1475.2006 and ANSI/AWWAB408.2003 The main differences are as follows.
--- This standard includes a liquid poly aluminum chloride, poly aluminum chloride and solid.
--- According to sources of raw materials and the production process technical progress of poly aluminum chloride and poly aluminum industry to improve the basicity of technical indicators.
There are changes in the relevant heavy metals --- Index test.
--- Deleted "ammonia nitrogen (N) determination."
This standard replaces GB 15892-2003 "water treatment agent poly aluminum chloride." The main differences between this standard and GB 15892-2003 are.
--- Standard name changed to "poly aluminum chloride in drinking water."
--- Table 1 Specifications are subject to change.
--- Increased CuSO4 standard solution titration test method alumina.
--- Revised some technical indicators measuring method.
--- Deleted "ammonia determination."
Appendix A of this standard is an informative annex.
The standard proposed by China Petroleum and Chemical Industry Association.
This standard by the National Standardization Technical Committee of Chemical Water Treatment Chemicals Branch (SAC/TC63/SC5) centralized.
This standard is drafted by. Run-Shenzhen Water Industry and Technology Development Co., Ltd., Tongji University, Taicang City, Jiangsu star light additives plant,
Shenzhen, Qingyuan water purification equipment Co., Ltd., Shandong Lu net Chemical Co., Kemira Water Technologies (Chongqing) Co., Ltd., Dongguan City,
Clean Water Material Co., Ltd., Jiaozuo City, Ireland Fokker Ltd., Henan Hua Quan water plant material Henan new century purification materials
Limited.
Participated in the drafting of this standard. CNOOC Tianjin Chemical Research & Design Institute, Wuxi will Sheng water treatment agent Co., Wuhan City in the run fine
Fine Chemicals Co., Ltd., Gongyi City Shibata purification plant, Yu Gongyi City clean water Materials Co., Ltd. Gongyi City Fuyuan water purification materials Limited
Secretary, Chongqing University, Ningbo Huaguang Industrial Company Purifying Agent.
The main drafters of this standard. Li Runsheng, Li Fengting, Taofu Tang, Zhang civil rights, Jia Jiushun, Zou Peng, Wang Longqing, Xu Zhiyuan, Yuan Mengbin,
Iron your waves.
This standard replaces the standards previously issued as follows.
--- GB 15892-1995, GB 15892-2003.
Drinking poly aluminum chloride
1 Scope
This standard specifies the use of poly aluminum chloride in drinking water requirements, test methods, inspection rules, packaging, labeling, transport and storage.
This standard applies to drinking water with poly aluminum chloride. The product is mainly used for drinking water purification. Production of poly aluminum chloride feed
Hydrochloric acid, the industrial synthesis of hydrochloric acid should be used; aluminum-containing materials should be used in industrial aluminum hydroxide, kaolin clay, a boehmite, gibbsite and water treatment agent
Aluminum calcium.
Exemplary formula. Al shape (OH) m1 Cl (3 shape - m1) 0 < m1 < 3 like
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 191 Packaging - Pictorial signs
Preparation of GB/T 601 chemical reagent standard titration solution
Preparation of standard solution of GB/T 602 chemical reagent determination of impurities (GB/T 602-2002, ISO 6353-1. 1982, NEQ)
GB/T 603 chemical reagent test methods in the formulation and preparation of products (GB/T 603-2002, ISO 6353-1 with. 1982,
NEQ)
GB/T 610 General method for determination of arsenic Chemicals (GB/T 610-2008, ISO 6353-1. 1982, NEQ)
GB/T 6678 General Principles for Sampling Chemical Products
GB/T 6682 analytical laboratory use specifications and test methods (GB/T 6682-2008, ISO 3696. 1987, MOD)
GB/T 8946 plastic bags
3 Product Categories
Poly aluminum chloride according to patterns divided into two types of liquids and solids.
4 Requirements
4.1 Appearance
Liquid. colorless to yellow-brown liquid.
Solid. white to brown powder or granules.
4.2 poly aluminum chloride in drinking water indicators should meet the requirements of Table 1.
Table 1
Index Name
index
Liquid Solid
Alumina (Al2O3) mass fraction /% ≥ 10.0 29.0
Basicity/40.0 to 90.0%
Density (20 ℃) \u200b\u200b/ (g/cm3) ≥ 1.12 -
Insolubles content /% ≤ 0.2 0.6
......
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