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GB/T 42391-2023Electrolyte for lead acid storage battery (English PDF)

铅酸蓄电池用电解液

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Issued by

SAMR; SAC

Level / Type

National · Recommended

Issue date

March 17, 2023

Implementation date

October 1, 2023

Scope

GB/T 42391-2023 is the English-translated version of 铅酸蓄电池用电解液.

GB/T 42391-2023 covers the electrolyte a lead acid storage battery is filled with, dilute sulfuric acid and colloidal electrolyte alike. Requirements are stated first, and then the determination methods, which occupy most of the document: the analytical procedures by which the properties set in the requirements clause are measured, so that two parties testing the same drum reach the same verdict. Inspection rules reach back to the ingredients, since the electrolyte can be no better than what goes into it — the concentrated sulfuric acid used to prepare it has to meet HG/T 2692, and the water used to dilute it is specified as well. Marking, packaging, transportation and storage fix what the container states: manufacturer name and address, product name, trademark, grade, specification, date, batch number and net weight. A safety clause covers handling, with pouring or conduit discharge to keep impurities out, and protective glasses, gloves and clothing because sulfuric acid is corrosive and burnable. Appendix A tabulates concentration against density, the link between a hydrometer reading taken on the floor and the concentration a specification is written in. Contamination is the practical reason for the document: a filled battery cannot be rinsed out, and whatever came in with the acid stays for the life of the cell. For electrolyte producers, battery manufacturers, incoming inspection laboratories and purchasers.

Document preview — GB/T 42391-2023

National Standard of the People's Republic of China

ICS
29.220.20
Classification
K84

Issued by: State Administration for Market Regulation; Standardization Administration of the PRC

Contents

  • Foreword3
  • 1 Scope6
  • 2 Normative References6
  • 3 Terms and Definitions7
  • 4 Requirements7
  • 5 Determination Method8
  • 6 Inspection Rules21
  • 7 Marking, Packaging, Transportation and Storage22
  • 8 Safety Requirements22
  • Appendix A (informative) Comparison of Concentration and Density of Sulfuric Acid23

Foreword

This document was issued on 17 March 2023 by the State Administration for Market Regulation; Standardization Administration of the PRC and takes effect on 1 October 2023.

It is a GB/T standard: recommended rather than compulsory, but it is the text a Chinese reviewer applies when assessing a submission.

1 Scope

GB/T 42391-2023 covers the electrolyte a lead acid storage battery is filled with, dilute sulfuric acid and colloidal electrolyte alike. Requirements are stated first, and then the determination methods, which occupy most of the document: the analytical procedures by which the properties set in the requirements clause are measured, so that two parties testing the same drum reach the same verdict. Inspection rules reach back to the ingredients, since the electrolyte can be no better than what goes into it — the concentrated sulfuric acid used to prepare it has to meet HG/T 2692, and the water used to dilute it is specified as well. Marking, packaging, transportation and storage fix what the container states: manufacturer name and address, product name, trademark, grade, specification, date, batch number and net weight. A safety clause covers handling, with pouring or conduit discharge to keep impurities out, and protective glasses, gloves and clothing because sulfuric acid is corrosive and burnable. Appendix A tabulates concentration against density, the link between a hydrometer reading taken on the floor and the concentration a specification is written in. Contamination is the practical reason for the document: a filled battery cannot be rinsed out, and whatever came in with the acid stays for the life of the cell. For electrolyte producers, battery manufacturers, incoming inspection laboratories and purchasers.

This document specifies the requirements, determination methods, inspection rules, marking,

packaging, transportation, storage and safety requirements of the electrolyte (including

colloidal electrolyte) for lead acid storage battery.

This document is applicable to the electrolyte (including colloidal electrolyte) for lead acid

storage battery.

This document does not apply to the electrolyte in lead acid storage battery after disassembly.

2 Normative References

The contents of the following documents constitute indispensable clauses of this document

through the normative references in the text. In terms of references with a specified date, only

versions with a specified date are applicable to this document. In terms of references without a

specified date, the latest version (including all the modifications) is applicable to this document.

GB 190 Packing Symbol of Dangerous Goods

GB/T 622 Chemical Reagent - Hydrochloric Acid (GB/T 622-2006, ISO 6353-2:1983, NEQ)

GB/T 625 Chemical Reagent - Sulfuric Acid (GB/T 625-2007, ISO 6353-2:1983, NEQ)

GB/T 626 Chemical Reagent - Nitric Acid (GB/T 626-2006, ISO 6353-2:1983, NEQ)

GB/T 629 Chemical Reagent - Sodium Hydroxide

GB/T 643 Chemical Reagent - Potassium Permanganate (GB/T 643-2008, ISO 6353-2:1983,

NEQ)

GB/T 661 Chemical Reagent - Ammonium Iron (II) Sulfate Hexahydrate (GB/T 661-2011, ISO

6353-3:1987, NEQ)

GB/T 670 Chemical Reagent - Silver Nitrate (GB/T 670-2007, ISO 6353-2:1983, NEQ)

GB 1253 Working Chemical - Sodium Chloride

GB 1254 Working Chemical - Sodium Oxalate

GB 1257 Working Chemical - Potassium Hydrogen Phthalate

GB 12595 Working Chemical - Silver Nitrate

In a brightly lit room, conduct a visual inspection on whether the surface of the sample is

colorless and transparent.

5.2.2 Density

5.2.2.1 Instrument

Density meter: with a division value of  0.001 g/cm3.

5.2.2.2 Determination steps

Take 250 mL of the specimen in 5.1.2.1, stir it well, then, transfer it into a 250 mL measuring

cylinder; put it in a water bath at 25 C, let it stand for 20 min. Gently put the density meter

into the specimen, wait until it stops sinking, visually observe the tangent line of the concave

surface of the liquid, and read the value on the density meter.

The test result shall retain three decimal places.

5.2.3 Determination of sulfuric acid content

5.2.3.1 Principle

Weigh-take or absorb a certain amount of specimen, and use methyl red-methylene blue as a

mixed indicator. The end point of titration is pH = 5.4, and the solution turns from purple red

to gray green, and the color variation is sensitive and easy to judge.

5.2.3.2 Reagents and solutions

The reagents and solutions required for the test are as follows:

---Methyl red-methylene blue mixed indicator: one portion of 0.2% methyl red ethanol

solution is mixed with one portion of 0.1% methylene blue ethanol;

---Potassium hydrogen phthalate (GB 1257): benchmark reagent;

---Phenolphthalein: analytically pure, 0.1% ethanol solution;

---Sodium hydroxide (GB/T 629): analytically pure, standard solution of C (NaOH) = 0.5

mol/L.

a) Preparation: prepare a saturated solution of sodium hydroxide and store it in a plastic

bottle, seal it and place it, until the solution becomes clear. Take 26 mL of the

supernatant and place it in 1,000 mL of carbon dioxide-free water, and mix it well;

b) Calibration: weigh-take 3 g (accurate to 0.0001 g) of benchmark potassium hydrogen

phthalate dried at 105 C ~ 110 C for 2 h, put it in a 250 mL conical flask, add 80

mL of water and heat it to boiling. Dropwise add 2 drops ~ 3 drops of 0.1%

phenolphthalein indicator, and use sodium hydroxide solution of C (NaOH) = 0.5

mol/L to titrate it, until the solution turns pink, which is the end point.

5.2.4 Determination of reduced potassium permanganate (calculated by O) content

5.2.4.1 Principle

Inject excess potassium permanganate solution into the specimen to thoroughly oxidize the

reducing substance; use ferrous ammonium sulfate solution to perform back titration, so as to

obtain the content of reduced potassium permanganate.

5.2.4.2 Reagents and solutions

The reagents and solutions required for the test are as follows:

---Sulfuric acid (GB/T 625): analytically pure, 1 + 1 solution and solution with a density

of 1.200 g/cm3;

NOTE: see Appendix A for the comparison of the concentration and density of sulfuric acid.

---Sodium oxalate (GB 1254): benchmark reagent;

---Ferrous ammonium sulfate solution (GB/T 661): analytically pure, C [(NH4)2Fe(SO4)2]

= 0.01 mol/L. Weigh-take 4 g of (NH4)2Fe(SO4)2  6 H2O and dissolve in 100 mL of 1

+ 1 sulfuric acid solution, and use water to dilute to 1,000 mL;

---Potassium permanganate standard solution (GB/T 643): analytically pure, C (1/5

KMnO4) = 0.1 mol/L. This standard solution is used to prepare a standard solution of

C (1/5 KMnO4) = 0.01 mol/L.

a) Preparation: weigh-take 3.30 g of potassium permanganate, dissolve it in 1,050 mL

of water, slowly boil it for 20 min ~ 30 min and place it in the dark for a week. Use

glass wool to filter it, and store the filtrate in a brown bottle with a ground stopper.

b) Calibration: weigh-take 0.2 g of benchmark sodium oxalate dried at 105 C ~ 110 C

for 2 h, accurate to 0.0001 g, and dissolve it in 50 mL of pure water. Add 8 mL of

concentrated sulfuric acid, use potassium permanganate standard solution of C (1/5

KMnO4) = 0.1 mol/L to titrate it, and when it approaches the end point, heat to 70 C

~ 80 C, continue titration, until the solution turns pink and maintains for 30 s,

meanwhile, carry out a blank test.

c) Calculation: the concentration of 0.1 mol/L potassium permanganate solution of C

(1/5 KMnO4) shall be calculated in accordance with Formula (3).

Where,

m---the mass of the weighed sodium oxalate, expressed in (g);

V---the volume of potassium permanganate solution used, expressed in (mL);

M (1/2 Na2C2O4)---the mass of 0.5 mol of sodium oxalate, expressed in (g/mol).

d) Preparation of 0.01 mol/L potassium permanganate standard solution: use pure water

to accurately dilute the prepared potassium permanganate standard solution of C (1/5

KMnO4) = 0.1 mol/L to C (1/5 KMnO4) = 0.01 mol/L.

5.2.4.3 Instruments

Commonly used laboratory instruments: 250 mL conical flask and burette, etc.

5.2.4.4 Determination steps

5.2.4.4.1 Correction of ratio

The ratio of the volume (mL) of potassium permanganate standard solution of C (1/5 KMnO4)

= 0.01 mol/L to the volume (mL) of ferrous ammonium sulfate solution of C [(NH4)2Fe(SO4)2]

= 0.01 mol/L, expressed in K, shall be corrected by the following method and calculated in

accordance with Formula (4).

Weigh-take 40 g (accurate to 0.001 g) of diluted sulfuric acid with a density of 1.200 g/cm3 (the

average value of the electrolyte density, so that the reaction is carried out at the same acidity),

place it in a 250 mL conical flask. Use a burette to accurately add 10 mL of potassium

permanganate standard solution of C (1/5 KMnO4) = 0.01 mol/L, and use 0.01 mol/L ferrous

ammonium sulfate solution to perform the titration.

Where,

V---the volume of potassium permanganate standard solution used, expressed in (mL);

V1---the volume of ferrous ammonium sulfate solution used, expressed in (mL).

5.2.4.4.2 Determination of specimen

Weigh-take 40 g (accurate to 0.001 g) of the specimen in 5.1.2.1, place it in a 250 mL conical

flask; use a burette to accurately add 10 mL of potassium permanganate standard solution of C

(1/5 KMnO4) = 0.01 mol/L and heat to 70 C ~ 80 C. Stop heating, and cool to room

temperature, (when the specimen appears discolored, re-sampling shall be considered, and the

quantity of specimens to be weighed shall be reduced) accurately add 10 mL of ferrous

ammonium sulfate solution of C [(NH4)2Fe(SO4)2] = 0.01 mol/L. Immediately use potassium

permanganate standard solution of C (1/5 KMnO4) = 0.01 mol/L to titrate it, until it turns light

purple red, which is the end point.

5.2.4.5 Result calculation

solution contains 0.5 mg of chlorine; Solution B: 1 mL of standard solution contains

0.05 mg of chlorine.

Solution A: accurately weigh-take 0.8245 g of benchmark sodium chloride burned at

500 C ~ 600 C for 1 h, dissolve it in 50 mL of water, then, transfer it into a 1,000 mL

volumetric flask; use water to wash it and dilute to the scale, then, shake it well.

Solution B: accurately draw 10 mL of Solution A and put it in a 100 mL volumetric

flask; use water to dilute to the scale, and shake it well.

5.2.5.3 Instruments

Commonly used laboratory instruments: 50 mL colorimetric tube, 100 mL volumetric flask and

1,000 mL volumetric flask, etc.

5.2.5.4 Determination steps

5.2.5.4.1 Preparation of standard color gradation

Successively add 0.0 mL, 0.4 mL, 0.8 mL, 1.2 mL, 1.6 mL and 2.0 mL of chlorine standard

solution B to six 50 mL colorimetric tubes, then, use a pipette to add 30 mL of chlorine-free

diluted sulfuric acid with the same density as the specimen. Then, respectively add 2 mL of 1

+ 4 nitric acid and 2 mL of 2% silver nitrate, and shake it well. Place it in the dark for 20 min.

5.2.5.4.2 Determination of specimen

Weigh-take 30 g of specimen in a 50 mL colorimetric tube, accurate to 0.001 g (m); add 2 mL

of 1 + 4 nitric acid and 2 mL of 2% silver nitrate. Compare it with the standard color gradation,

and adopt the method of visual turbidimetry to determine the chlorine content.

5.2.5.5 Result calculation

The chlorine content, which is expressed in mass fraction X3 and mg/L, shall be calculated in

accordance with Formula (6):

Where,

m1---the chlorine content of the chlorine standard solution with the same turbidity as the

specimen, expressed in (mg);

m---the mass of the specimen, expressed in (g);

rho---the density of the specimen, expressed in (g/cm3).

The calculation result shall retain three decimal places.

5.2.6 Determination of iron, copper, manganese, nickel, antimony, bismuth, cadmium,

cobalt, zinc and chromium content

5.2.6.1 Instrument

Atomic absorption spectrophotometer.

5.2.6.2 Preparation of standard solution

The preparation of standard solution is shown in Table 3.

5.2.6.3 Specimen preparation

Use an elongated pipette to take 20 mL of the sample in 5.1.2.1 in a 250 mL volumetric flask,

dilute it to the scale, and take the blank solution as a reference. On the atomic absorption

spectrophotometer, use the acetylene-air flame, and in accordance with the wavelengths in

Table 3, successively determine the concentration of the blank C0 and the specimen C1.

5.2.6.4 Result calculation

The iron, copper, manganese, nickel, antimony, bismuth, cadmium, cobalt, zinc and chromium

content shall be calculated in accordance with Formula (7):

Where,

C x---the concentration of a certain element specimen, expressed in (mg/L);

C1---the read concentration in the determination of a certain element, expressed in (g/mL);

C0---the blank concentration in the determination of a certain element, expressed in (g/mL);

n---the dilution ratio of the specimen (take 12.5).

5.2.7 Determination of titanium, mercury, tin and selenium content

5.2.7.1 Instrument

Inductively coupled plasma emission spectrometer (ICP).

5.2.7.2 Preparation of standard solution

See the preparation of standard solution in Table 3.

5.2.7.3 Specimen preparation

Use an elongated pipette to take 20 mL of the sample in 5.1.2.1 in a 250 mL volumetric flask,

dilute it to the scale, and take the blank solution as a reference. On the inductively coupled

plasma emission spectrometer, successively determine the concentration of the blank C0 and

5.3 Determination Method for Colloids

5.3.1 Appearance

In a brightly lit room, conduct a visual inspection on whether the color of the appearance of the

specimen is uniform.

5.3.2 pH

Take a piece of pH test paper universal, dip it into the specimen, after 1 s, take it out, compare

it with the standard color plate and read the pH.

The test result shall retain an integer.

5.3.3 Density

5.3.3.1 Instrument

Density meter: 1.000 g/cm3 ~ 2.000 g/cm3, with a division value of 0.005 g/cm3.

5.3.3.2 Determination steps

Take 250 mL of the specimen in 5.1.2.2, thoroughly stir it, then, transfer it into a 250 mL

graduated cylinder. Place the graduated cylinder in a water bath at 25 C  1 C and maintain

the temperature constant; let it stand for 20 min, so that the air bubbles can overflow. Gently

put the density meter into the test solution, wait for it to stop sinking, then, visually observe the

tangent line of the concave surface of the specimen solution, and read the value on the density

meter.

The test result shall retain three decimal places.

5.3.4 Determination of silicon dioxide content

5.3.4.1 Instrument

High-temperature chamber electric resistance furnace, with the temperature controlled at 950

C ~ 1,000 C.

5.3.4.2 Reagent and solution

Hydrochloric acid (GB/T 622): analytically pure, with a density of 1.190 g/cm3.

5.3.4.3 Determination steps

Weigh-take 10 g of specimen (accurate to 0.0001 g) in a 120 mL porcelain, slowly add 10 mL

of concentrated hydrochloric acid with a density of 1.190 g/cm3. Place the solution on a water

bath at 80 C, heat and concentrate it to dryness, steam it for 1 h, then, remove and cool it. Add

5 mL of concentrated hydrochloric acid, heat it to slight boiling, then, add 20 mL of hot water,

and immediately use a medium-speed quantitative filter paper to filter it into a 250 mL

volumetric flask (the filtrate can be used for the determination of impurities, for example, iron).

Use hot water to wash the precipitate and the filter paper, until there is no chloride ion (use

silver nitrate to test it); use water to dilute it to the scale and shake it well.

Place the precipitate and the filter paper in a porcelain crucible with a constant mass and

carefully incinerate it. In the high-temperature chamber electric resistance furnace at 950 C ~

1,000 C, burn it for 30 min, then, place it in a desiccator to cool to room temperature, until

reaching a constant mass (otherwise, the burning shall be performed again).

5.3.4.4 Result calculation

The content of silicon dioxide, which is expressed in mass fraction X4, shall be calculated in

accordance with Formula (9):

Where,

G1---the dry weight of the precipitate of silicon dioxide, expressed in (g);

G---the weight of the specimen, expressed in (g).

The calculation result shall retain an integer.

5.3.5 Determination of iron content

See 5.2.6.

NOTE: when being transferred to a 250 mL volumetric flask, the colloidal specimens need to be

filtered.

5.3.6 Determination of chlorine content

5.3.6.1 Instruments and equipment

The instruments and equipment required for the test are as follows:

---High-temperature chamber electric resistance furnace, with the temperature controlled

at 500 C ~ 600 C;

---Constant-temperature drying oven.

5.3.6.2 Reagents and solutions

The reagents and solutions required for the test are as follows:

---Potassium chromate (HB/T 3440): analytically pure, 5% solution. Weigh-take 5 g

(accurate to 0.1 g) of potassium chromate, and dissolve it in a small amount of water;

(the instrument needs to be calibrated before use).

Remaining clauses in the full document

  • 3 Terms and Definitions
  • 4 Requirements
  • 5 Determination Method
  • 6 Inspection Rules
  • 7 Marking, Packaging, Transportation and Storage
  • 8 Safety Requirements

......
This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 23 pages — is available in the English PDF.

Referenced standards

Normative references

GB 190 Packing Symbol of Dangerous Goods · GB/T 622 Chemical Reagent - Hydrochloric Acid (GB/T 622-2006, ISO 6353-2:1983, NEQ) · GB/T 626 Chemical Reagent - Nitric Acid (GB/T 626-2006, ISO 6353-2:1983, NEQ) · GB/T 643 Chemical Reagent - Potassium Permanganate (GB/T 643-2008, ISO 6353-2:1983, · GB/T 661 Chemical Reagent - Ammonium Iron (II) Sulfate Hexahydrate (GB/T 661-2011, ISO · GB/T 670 Chemical Reagent - Silver Nitrate (GB/T 670-2007, ISO 6353-2:1983, NEQ)

Similar standards

GB 38031-2025|GB 190|GB/T 622|GB/T 622-2006|GB/T 625|GB/T 625-2007|GB/T 626|GB/T 626-2006

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