IS 2411 (1963): Methods of chemical analysis of fluorspar ...crucible of fine porosity, avoiding...

23
Disclosure to Promote the Right To Information Whereas the Parliament of India has set out to provide a practical regime of right to information for citizens to secure access to information under the control of public authorities, in order to promote transparency and accountability in the working of every public authority, and whereas the attached publication of the Bureau of Indian Standards is of particular interest to the public, particularly disadvantaged communities and those engaged in the pursuit of education and knowledge, the attached public safety standard is made available to promote the timely dissemination of this information in an accurate manner to the public. इंटरनेट मानक !ान $ एक न’ भारत का +नम-णSatyanarayan Gangaram Pitroda “Invent a New India Using Knowledge” प0रा1 को छोड न’ 5 तरफJawaharlal Nehru “Step Out From the Old to the New” जान1 का अ+धकार, जी1 का अ+धकारMazdoor Kisan Shakti Sangathan “The Right to Information, The Right to Live” !ान एक ऐसा खजाना > जो कभी च0राया नहB जा सकता ह Bharthari—Nītiśatakam “Knowledge is such a treasure which cannot be stolen” IS 2411 (1963): Methods of chemical analysis of fluorspar (fluorite) [MTD 13: Ores and Raw Materials]

Transcript of IS 2411 (1963): Methods of chemical analysis of fluorspar ...crucible of fine porosity, avoiding...

Page 1: IS 2411 (1963): Methods of chemical analysis of fluorspar ...crucible of fine porosity, avoiding contact with rubber or other organic material. Store in a dark coloured glass bottle.

Disclosure to Promote the Right To Information

Whereas the Parliament of India has set out to provide a practical regime of right to information for citizens to secure access to information under the control of public authorities, in order to promote transparency and accountability in the working of every public authority, and whereas the attached publication of the Bureau of Indian Standards is of particular interest to the public, particularly disadvantaged communities and those engaged in the pursuit of education and knowledge, the attached public safety standard is made available to promote the timely dissemination of this information in an accurate manner to the public.

इंटरनेट मानक

“!ान $ एक न' भारत का +नम-ण”Satyanarayan Gangaram Pitroda

“Invent a New India Using Knowledge”

“प0रा1 को छोड न' 5 तरफ”Jawaharlal Nehru

“Step Out From the Old to the New”

“जान1 का अ+धकार, जी1 का अ+धकार”Mazdoor Kisan Shakti Sangathan

“The Right to Information, The Right to Live”

“!ान एक ऐसा खजाना > जो कभी च0राया नहB जा सकता है”Bhartṛhari—Nītiśatakam

“Knowledge is such a treasure which cannot be stolen”

“Invent a New India Using Knowledge”

है”ह”ह

IS 2411 (1963): Methods of chemical analysis of fluorspar(fluorite) [MTD 13: Ores and Raw Materials]

Page 2: IS 2411 (1963): Methods of chemical analysis of fluorspar ...crucible of fine porosity, avoiding contact with rubber or other organic material. Store in a dark coloured glass bottle.
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IS : 2411 - 1963 ( Reaffirmed 1996 )

Indian Standard METHODS OF CHEMICAL

ANALYSIS OF FLUORSPAR ( FLUORITE )

( Third Reprint March 1997 )

UDC 543 : 553.634

0 Copyright 1963

Gr 6

BUREAU OF INDIAN STANDARDS MANAK BHAVAN. 9 BAHADUR SHAH ZAFAR MARG

NEW DELHI 110002

.4 ugust 1963

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Indian Standard

IS:2411 - 1963

METHODS OF CHEMICAL

ANALYSIS OF FLUORSPAR ( FLUORITE )

Methods of Chemical Analysis Sectional Committee, SMDC 2

Chairman

DR. T. BAXERJEE

Representing

National Metalhfrgical Laboratory (CSIR ), Jamshedpur

DR. H. P. BHATTACHABYA ( Alternale to Dr. T. Banerjee )

SH~I K. L. BANERJE~ Refractories Sectional Committee, SMDC 18, IS1 DR. M. K. BOSE Assay Department ( Ministry of Finance ).

Calcutta DR. G. P. CEATTEI~JEE Hindustan Steel Ltd., Durgapur Steel Plant,

Durgapur SHBI A. C. BHOWMIK ( ,4ltemnte )

DEE,UTY DIBECTOR RESEARCB Research, Designs & Standards Organization (M&C) ( Ministry of Railways ). Chittaranjan

SHRI J. P. SAXENA ( Ahwmre~ DR. R. K. DUTTA Defence Metallurgical Research Laboratory

[ Ministry of Defence ( R & D ) 1, Ishapur SHRI D. N. ELCEIDAXA Italab Private Ltd., Bombay

SIKRI S. S. HONAVAR ( Alternate ) SRRI B. B. GHOSAL Indian Iron & Steel Co. Ltd., Burnpur

SHRI J. N. BARMAN ( AIlemate ) SHRI C. R. GOIL Ferro Alloys Corpor%ion Ltd., Tumsar

( Maharashtra ) SFIRI A. SANGAMESFIWA~A RAO ( Alternate )

DR. S. KUMAR Central Glass & Ceramic Research Institute ( CSIR ), Calcutta

SHRI B. K. AGARWAL ( Allemate ) SHRI D. R. MALIK Director General, Ordnance Factories ( Ministry

of Defence ), Calclitta SHRI R. N. DATTA ( Alkrnate)

SERI M. M. MOVDQILL Indian Non-Ferrous Metals Manufacturers’ Association, Calcutta

SERI N. MAJUMDAR ( &?ernute )

(Continued on page 2 )

BUREAU OF INDIAN STANDAR’DS MANAK BHAVAN, 9 BAHADUR SHAH ZAFAR MARC

NEW DELHI 110002

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IS:2411-1963

( Continued from page 1)

Members Reprewnting

DE. G. V. L. N. MIJBTY The Tata Iron BE Steel Co. Ltd., Jamshedpur SHBI H. P. SAMA~TA ( AECetnale )

SHBI N. C. SEN GUPTA Government Test House, Calcutta SHBI P. R. SUBBABAMAN National Chemical Laboratory ( CSIR ). Poona

DB. J. L. BOSE ( Alternate ) SEBI B. S. KBISHNAMACHAR, Director, ISI ( Ex-o&50 Member )

Deputy Director ( S & M )

Secretary

SHIU S. L. BALX

Extra Assistant Director ( S & M )

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IS:24ll-1963

CONTENTS

0.

1.

2.

3.

4.

5.

6.

7.

8.

9.

10.

11.

12.

13.

FOREWORD . . . . . . . . . . . . . . .

PAGE

4

SCOPE . . . . . . . . . . . . . . .

SAMPLING . . . . . . _. . . . . . . .

QUALITY OF REAGENTS . . . 6. . . . . _ . . .

GENERAL . . . . . . . . . . . . . . .

DETERMINATION OF CALCIUM FLUORIDE BY THE VOLUMETRIC METHOD . . . . . . . . . . . . . . . 6

DETERMINATION OF CALCIUM AS CALCIUM CARBONATE BY THE DECOMPOSITION METHOD . . . . . . . . . ‘8

DETERMINATION OF CALCIUM AS CALCIUM CARBONATE BY THE ACETATE ( ALTERNATE) METHOD (APPLICABLE TO FLUORSPAR FREE FROM LEAD AND ZINC ) . . . . . . . . .

DETERMINATION OF SILICA BY THE GRAVIMETRIC METHOD . . .

11

11

DETERMINATION OF MIXED OXIDES ( Fe&&, A&O,, etc) BY AMMONIUM HYDROXIDE PRECIPITATION METHOD . . . 12

DETERMINATION 01; BARIUM AS SULPHATE BY THE GRAVIMETRIC METHOD . . . . . . . . . . . . . . . 14

DETERMINATION OF LEAD AS SULPHIDE BY THE GRAVI~IETRIC METHQD . . . . . . . . . . . . . . . 15

DETERMINATION OF ZINC AS SULPHIDE BY THE GRAVIMETRIC METHOD . . . . . . . . . . . . . . . . 16

DETERMINATION OF SULPHUR BY THE GRAVIMETNC &~ETH~D 17

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IS : 2411 - 1963

Indian Standard METHODS OF CHEMICAL

ANALYSIS OF FLUORSPAR ( FLUORITE )

0. FOREWORD

0.1 This Indian Standard was adopted by the Indian Standards Institu- tion on 10 June 1963, after the draft finalized by the Methods of Chemical Analysis Sectional Committee had been approved by the Structural and Metals Division Council.

0.2 Fluorspar is used in steel making; manufacture of ferro alloys; foundry work; smelting of silver, copper and lead ores; electrolytic refining of antimony and lead; and in the manufacture of hydrofluoric acid, fluorine, etc. In steel making, it is added to metal bath to promote slag fluidity and in the basic process to assist in the removal of sulphur and phos- phorus. It usually contains 85 percent or more of calcium fluoride. Two grades commonly used in various industries are metallurgical and acid grades and, in order to evaluate the grades of fluorite, it is necessary that correct analysis of calcium fluoride, silica, calcium carbonate, etc, should be made. Since various laboratories in India follow different procedures and the results reported, therefore, may not always be comparable, neces- sity was felt for prescribing standard methods for the analysis of both metallurgical and acid grades, which could primarily serve as referee methods and could also be used by the laboratories for their day to day work.

0.3 The methods of analysis prescribed in this standard have been prepared with a view that they shall be useful as referee methods. Due considera- tion has been given in the preparation of this standard to the facilities available in the country for such analysis.

0.4 Taking into consideration the views of producers, consumers and test- ing authorities, the Sectional Committee responsible for the preparation of this standard felt that it should be related to the technological methods followed in the country in this field. Assistance has been derived from the following books:

FURMAN, N. H. ( En), .AND SCOTT, W. W. Standard Methods of Chemical Analysis, 5th ed. New York. D Van Nostrand Company, Inc., 1948.

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IS : 2411- 1963

LUNDELL, G. E. F., HOFFMAN, J. I., AND BRIGHT, H. F. Chemical Analysis of Iron and Steel. New York. John Wiley and Sons, Inc., 1946.

0.5 Wherever a reference to any Indian Standard appears in this standard, it shall be taken as a reference to the latest version of the standard.

0.6 In reporting the result of a test or analysis made in accordance with this standard, if the final value,observed or calculated, is to be rounded off, it shall be done in accordance with IS : 2-1960 Rules for Rounding Off Numerical Values ( Revised).

1. SCOPE

1.1 This standard prescribes the methods for determination of calcium fluoride, calcium carbonate, silica, mixed oxides, barium, lead, zinc and sulphur in fluorspar of metallurgical and acid grades within the following ranges:

2. SAMPLING

Calcium fluoride Calcium as calcium carbonate Silica Mixed oxides ( Fe203, A&O,, etc) Barium as’ sulphate Lead as sulphide Zinc as sulphide Sulphur

METALLURGICAL GRADE

Percent

Above 85 6 to 10 up to 5 1 to 2 up to 0.2 up to 0.5 up to 0.5 up to 0’3

ACID GRADE

Percent

Above 97 1 to 2 up to 1 0.1 to 0.5

- - - -

2.1 Laboratory Sample - In the analysis that follows, a truly representa- tive and homogeneous sample is essential. This shall be drawn and prepared in accordance with *IS : 2246- Methods of Sampling Fluorspar ( Fluorite ).

2.2 Test Sample - Grind sufficient quantity of the laboratory sample in an agate mortar. Dry at 105” to 110°C for one to two hours and use it for the purpose of chemical analysis.

‘Since published in 1963.

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IS : 2411 - 1963

3. QUALITY OF REAGENTS

3.1 Unless otherwise specified, pure chemicals and distilled water [see IS : 1070-1960 Specification for Water, Distilled Quality ( Revised )] shall be employed in the tests.

NOTE - ‘ Pure chemicals ’ shall mean chemic& that do not contain impurities which affeot the results of analysis.

4. GENERAL

4.1 Use of Filter Papers - In the methods prescribed in this standard, only relative numbers of Whatman filter papers have been prescribed since they are commonly used. However, any other suitable brand of filter paper of corresponding porosity may also be used.

5. DETERMINATION OF CALCIUM FLUORIDE BY THE VOLUMETRIC METHOD

5.1 Outline of the Method - The sample is boiled with acetic acid and filtered to remove calcium carbonate. The residue, after being hydro- fluorized to remove silica, is digested with hydrochloric acid and filtered. The filtrate is treated with hydrogen sulphide gas in ammoniacal medium, the precipitate filtered and calcium in the filtrate precipitated as oxalate, filtered, washed and determined volumetrically by titration with standard permanganate solution.

5.2 Reagents

5.2.1 Dilute Acetic Acid - 20 percent ( v/v ).

5.2.2 HydroJfuoric Acid - 40 percent.

5.2.3 Dilute Sulphuric Acid - 1 : I ( v/v ).

5.2.4 Concentrated Sulphuric Acid - sp-gr 1.84 [ conforming IS : 266-1961 Specification for Sulphuric Acid ( Revised) 1.

5.2.5 Dilute Hydrochloric Acid - 5 : 95 ( v/v ).

52.6 Concentrated Hydrochloric Acid - sp-gr 1.16 [conforming IS : 265-1962 Specification for Hydrochloric Acid ( Revised)].

5.2.1 Hydrogen Sulphide - gas.

5.2.8 Concentrafed Ammonium Hydroxide- 20 percent.

6

to

to

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,

5.2.9 Ammonium Chloride-Ammonium moderate stream of hydrogen sulphidle for

Sulphide Solution - Pass a 5 minutes through a solution

containing 5 ml of concentrated ammonium hydroxide and 10 g of ammonium chloride per litre.

IS : 2411 - 1963

5.2.10 Ammonium Oxalate - solid.

5.2.11 Standard Potassium Permanganate Solution - Dissolve 6.4 g of potassium permanganate in one litre of water. Let it stand for two weeks and filter without washing through a gooch crucible or fritted glass crucible of fine porosity, avoiding contact with rubber or other organic material. Store in a dark coloured glass bottle. Standardize against sodium oxalate as under 5.3.6.

5.3 Procedure

5.3.1 Weigh out accurately about 0.5 g of the sample and transfer to a 250-ml Erlenmeyer flask. Add about 20 ml of dilute acetic acid, insert a short-stemmed funnel in the neck of the flask as a splash trap and heat the mixture in a boiling water-bath for one hour, shaking from time to time. Wash the funnel with a small quantity of water. Dilute the SO~U- tion to 100 ml w?th warm water and bring to boil. Filter the solution through a No. 40 filter paper and tratisfer all the insoluble residue from the flask to the filter paper with a rubber-tipped glass rod. Wash the residue several times with hot water and reject the filtrate. Transfer the filter paper and the precipitate to a 30-ml platinum crucible. Dry and ignite at about 650% until all carbon is burnt off.

5.3.2 Treat the residue in the crucible with about 3 ml of hydrofluoric acid and evaporate to dryness. Add to it 4 ml of dilute sulphuric acid and evaporate to dryness. Cool, wash down the inside of the crucible with 2 ml or more of dilute sulphuric acid, in order to catch any un- decomposed particles of calcium fluoride, and again evaporate to dryness.

5.3.3 Cool the crucible and immerse it in a beaker containing 150 ml of dilute hydrochloric acid. Wash gently and remove the platinum crucible, cleaning it from adhering particles of calcium sulphate. Boil the contents of the beaker for 10 minutes. If insoluble matter remains, filter, wash and ignite the residue. Preserve the filtrate ( I ). The residue may consist of insoluble sulphates or undecomposed calcium fluoride. Treat the residue with a few drops of hydrofluoric acid and concentrated sul- phuric acid. Heat until they are expelled. Digest with one to two millilitres of concentrated hydrochloric acid on the steam-bath and filter. Mix this filtrate ( II ) with the filtrate ( I ) obtained above.

5.3.4 Pass hydrogen sulphide gas into the clear filtrate obtained under 5.3.3 and make the solution ammoniacal. Continue the current of

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IS:24ll-1963

gas for ten minutes and allow the precipitate to settle for 20 to 30 minutes. Filter and wash with ammonium chloride-ammonium sulphide solution. Neutralize the filtrate and washings with concentrated hydrochloric acid and add 20 ml of the acid in excess. Boil for two to three minutes to expel most of hydrogeu sulphide.

53.5 Concentrate the solution to 200 ml and add 2 g of ammonium oxalate followed by the gradual addition of concentrated ammonium hydroxide with stirring until the solution is slightly ammoniacal. Heat on a steam-bath for about an hour stirring occasionally. Filter the preci- pitate through a No. 40 filter paper and wash with hot water till free from oxalate. ’

5.3.6 Transfer the precipitate back to the beaker in which calcium was precipitated by pupcturing the filter paper, washing down with I5 ml of dilute sulphuric acid and finally with hot water to bring the calcium oxa- late into solution. Dilute the contents of the beaker to about 200 ml and heat to 75” to 80°C. Titrate with standard potassium permanganate solution until a stable pink colour is obtained.

5.4 Calculation

A x B x 2.80 $4.1 Calcium oxide, percent = ~_____

C

where

A = volume in ml of the standard permanganate solution consumed,

B = normality of the standard permanganate solution, and

C = weight in g of the sample taken.

5.4.2 Calcium fluoride, percent = CaO percent x l-3923 + 0.20 [O-20 is compensation factor for the loss of calcium fluoride ( CaF,)].

.6 DETERMINATION OF CALCIUM AS CALCIUM CARBONATE BY THE DECOMPOSITION METHOD

6.1 Outline of the Method - A known weight of the sample is made to react with an acid and the liberated carbon dioxide, freed from impurities, is absorbed in previously weighed soda asbestos bulbs and weighed. The difference in weights represents the weight of carbon dioxide in the sample from which calcium carbonate .is calculated.

6.2 Apparatus - The assembly of apparatus is shown in Fig. 1.

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A

A ---I -: _.

.-

_ --

NOTE -. Tubes are compactly arranged along from the table-top upon R tripod bs6e.

FIO. I ABSORPTION

the edge of 150 x 230 mm board which is supported 130 mm

TBAIN FOR CARBON DIOXIDE

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IS : 2411- 1963

6.3 Reagents

6.3.1 Dilute Hydrochloric Acid- 1 : 1 ( v/v ).

6.3.2 Concentrated Sulphutic Acid - see 5.2.4.

63.3 Ascarite or Soda Asbestos

6.3.4 Magnesium Perchlorate - solid.

6.3.5 Pumice Impregnated with Copper Sulphate - anhydrous. Crush pumice to approximately 6 mm size, sift free from dust, and transfer 60 g to a casserole. Cover with a concentrated solution of 30 to 35 g of copper sulphate, evaporate to dryness while constantly stirring, and then heat for 3 to 4 hours at 150” to 160°C in an air-bath. Cool in a desiccator, and preserve in a glass-stoppered bottle.

6.4 Procedure -Transfer one gram ofthe accurately weighed sample to the flask ( A ) and cover with water. Insert the stopper carrying the separatory funnel ( B ) and a condenser ( C ). Connect the latter with D, E and F. Pass air that is free from carbon dioxide through the system until it is judged that all carbon dioxide has been removed. Close the stopcock in the separatory funnel, and insert the weighed bulbs ( G ) and ( H ) in the train. Half fill the separatory funnel with dilute hydrochloric acid, replace the stopper carrying the air, and see that there is free passage for gases through the train. Open the stopcock in the separatory funnel and run acid into the flask slowly, if there is much carbon dioxide, and rapidly, if there is but a little. When effervescence diminishes in the former case, at once in the latter, start a flow of water in the con- denser, and heat the flask slowly so as to secure steady but quiet ebullition. When it is judged that carbon dioxide has been boiled out of the’ solution, remove the flame, increase the current of air, and sweep out all carbon dioxide. Disconnect the weighed bulbs, close the inlet and outlet tubes, and place them in the balance case. LVhen cool, open the stopper momentarily, and weigh against a similar tube used as counterpoise.

6.5 Calculation

Calcium carbonate, percent = ( B - A ) x 227.3 C

where

A = weight in g of the bulb before the test,

B = weight in g of the bulb after the test, and

C = weight in g of the sample taken.

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is : 2411- I%3

7. DETERMINATION OF CALCIUM AS CALCIUM CARBONATE BY THE ACETATE (ALTERNATE) METHOD (APPLICABLE TO FLUORSPAR FREE FROM LEAD AND ZINC)

7.1 Outline of the Method-Calcium carbonate in the sample is extracted by dilute acetic acid and it goes in solution as acetate, whereas calcium fluoride and silica remain practically unaffected. The residue is ignited and weighed.

7.2 Reagents -see 5.2.

7.3 Procedure - Weigh accurately 0’5 to 1-O g of the sample and proceed as described under 5.3.1. Ignite the residue at about 65O”C, cool in a desiccator and weigh. The loss of weight of the sample minus 0.002 g (which represents the weight of calcium fluoride soluble in acetic acid under the above conditions ) represents calcium carbonate in the sample.

7.4 Calculation

(A-0302) 100 Calcium carbonate, percent = -------Be-----

where

A = total loss of weight in g of the sample, and

B = weight in g of the sample taken.

8. DETERMINATION OF SILICA BY THE GRAVIMETRIC METHOD

8.1 Outliue qf the Method - After removal of carbonates by extraction of the sample with acetic acid, sulphides in the residue are first oxidized to sulphates and then removed by extraction with ammonium acetate solution. Silica is then determined by hydrofluorization of the residue as usual.

8.2 Reagents

8.2.1 Acetic Acid-Brdmine Mixture-Add 20 ml of liquid bromine to 80 ml of glacial acetic acid and mix thoroughly.

8.2.2 Potassium Bromide-Bromine Mixture - Transfer 500 g of liquid bromine to a’one-litre bottle, add about 700 ml of potassium bromide solution ( 20 percent) and shake carefully. Add more of the latter when the solution is exhausted.

8.23 Ammonium Acetate Solution - 50 percent ( w/v ).

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IS : 2411- 1963

8.2.4 HydrofIuoric Acid - 40 percent.

8.3 Procedure

8.3.1 Transfer one gram of the accurately weighed sample to an Erlenmeyer flask fitted with a funnel to serve as a splash trap. Add 3 ml of acetic acid-bromine mixture and digest on a boiling water-bath for 10 minutes. Add 10 ml of water and 10 ml of potassium bromide- bromine mixture and digest for 40 minutes on a boiling water-bath. Finally, add 10 ml of ammonium acetate solution and digest for 10 minutes. Filter hot through No. 40 filter paper. Wash well with 30 to 40 ml of hot water. Reject the filtrate.

8.3.2 Dry the insoluble residue, ignite at 650°C and weigh. Moisten the residue with water and break lumps, if any, with a glass rod. Add 5 ml of hydrofluoric acid and evaporate the mixture slowly and carefully to dryness. Repeat the treatment with hydrofluoric acid. (In case of high silica content, repeat this treatment until constant weight is obtained. ) Ignite the residue first at a low heat and then at 650°C for about 5 minutes. Cool in a desiccator and weigh. The loss in weight repre- sents silica content. Preserve the residue for the determination of mixed oxides (see 9 ).

8.4 Calculation

Silica, percent = $ X 100

where

A = loss in weight due to hydrofluorization of the residue, and

B = weight in g of the sample taken.

9. DETERMINATION OF THE MIXED OXIDES (Fe,O,, Al,O,, etc) BY AMMONIUM HYDROXIDE PRECIPITATION METHOD

9.1 Outline of the Method-The residue obtained after the removal of carbonates, sulphides and silica is heated to fumes with perchloric acid thereby converting all calcium fluoride along with other constituents to perchlorates, dissolved in dilute hydrochloric acid and filtered, if necessary. The residue is fused with sodium carbonate and dissolved in hydrochloric acid and mixed with the filtrate. Mixed oxides are then precipitated, filtered, ignited and weighed.

9.2 Reagents

9.2.1 Perchloric Acid- 70 percent.

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IS : 2411- 1963

9.2.2 Sodrum Carbonate -anhydrous.

9.2.3 Dilute Hjtdrochloric Acid- 1 : 1 ( v/v).

9.2.4 Ammonium Chloride - solid.

9.2.5 Methyl Red Indicator Solution - 0.1 percent ( w/v ).

9.2.6 Concentrated Ammonium Hydroxide - 20 percent.

9.2.7 Ammoniacal Ammonium Nitrate Solution - Dissolve one gram of ammonium nitrate in 100 ml of water and make it slightly -alkaline to methyl red with dilute ammonium hydroxide,( 1 : 1).

9.3 Procedure

93.1 Moisten the residue reserved under 8.3.2 in a platinum dish with 2 ml of water. Add 5 ml of perchloric acid and heat -it under a hood carefully. Continue heating until copious fumes are expelled. Repeat fuming with perchloric acid twice. Cool and dissolve in 150 ml of water containing 10 ml of concentrated hydrochloric acid by heating. If neces- sary, filter and wash with hot water. Preserve the filtrate.

9.3.2 Transfer the residue with the filter paper to a platinum crucible. Burn off the filter paper and ignite. Cool the crucible, add 2 g of sodium carbonate and fuse: Dissolve in dilute hydrochloric acid and mix with the filtrate reserved under 9.3.1.

9.3.3 Add about 10 g of ammonium chloride, 4 drops of methyl red indicator solution, bring to boil and slowly add concentrated ammonium hydroxide until the colour changes to yellow. Contmue boiling for a few minutes, allow to settle, fiiter and wash three times with ammoniacal ammonium nitrate solution. Dissolve the precipitate in hydrochloric acid, reprecipitate and filter as before. Wash the precipitate with hot ammoniacal ammonium nitrate solution until free from chloride. Dry and ignite the precipitate in a weighed platinum crucible at 1 000°C to constant weight.

9.4 Calculation

Mixed oxides ( Fe@,, A&O,, etc ), percent + 100

where

A = weight in g of the mixed oxides, and

B = weight in g of the sample taken.

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is : 2411- 1963

10. DETERMINATION OF BARIUM AS SULPHATE BY THE GRAVIMETRIC METHOD

10.1 Outline of the Method -The sample is treated with hydrofluoric acid, digested with perchloric acid and fumed. The fumed mass is taken up with dilute hydrochloric acid, the solution boiled, filtered and barium recovered from the residue left on the filter paper. Barium in the solution is then precipitated as barium sulphate.

10.2 Reagents

10.2.1 Hydrofluoric Acid - 40 percent.

10.2.2 Concentrated Nitric Acid - sp-gr 1.42 ( conforming to *IS : 264-1950 Specification for Nitric Acid ).

10.2.3

103.4

10.2.5

10.2.6

10.2.7

10.2.8

Perchloric Acid - 70 percent.

Dilute Hydrochloric Acid - 1: 1, 1 : 9 and 1 : 99 ( V,‘Y ).

Dilute Sulphuric Acid - 1 : i and 1 : 3 ( v/v ).

Sodium Carbonate - anhydrous.

Concentrated Ammonium Hydroxide - 20 percent.

Ammonium Acetate Solution - 20 percent ( nl;v ).

10.3 Procedure

10.3.1 Weigh accurately 5 g of the sample and transfer to a platinum dish. Digest on a steam-bath for 10 minutes with 10 ml of hydrofluoric acid. Add more hydrofluoric acid if the sample is highly siliceous. Add 5 ml of concentrated nitric acid and 25 ml of perchloric acid and evaporate to fuming. Repeat the addition of’ perchloric acid and again fume. Take up the fumed mass in 50 ml of dilute hydrochloric acid ( 1 : 9 ) and heat to boiling. If residue remains, filter and wash with- warm water. Preserve the filtrate.

10.3.2 I.gnite the residue at dull red heat and treat with 5 to 10 ml of hydrofluorlc acid and 5 to 10 drops of dilute sulphuric acid ( 1 : 1 >. Evaporate the acids at a low temperature, fuse with sodium carbonate and extract the melt with water. Filter, wash the paper and residue with hot water, dissolve the residue in hydrochloric acid and acid the clear solution to the filtrate reserved under 10.3.1. Dilute the combined solu- tion to 200 ml and neutralize the solution with ammonidm hydroxide till just alkaline. Re-acidify with dilute hydrochloric acid ( 1 : 1 ), adding

*Since revised.

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IS : 2411 - 1963

2 ml in excess. Heat to boiling and add dropwise and with stirring 4 ml of dilute sulphuric acid ( 1 : 3 ). Boil for 15 minutes and digest on steam- bath for 3 to 4 hours. Do not allow the solution to cool below 50°C because of the tendency of calcium sulphate to separate. If any precipitate forms, filter, wash with hot dilute hydrochloric acid ( 1 : 99) and then with cold water. Preserve the filtrate for determination of lead and zinc, if any (see 11 and 12 ). Ignite the precipitate and we.igh as barium sulphate.

x0.3.2.1 If lead is present in an appreciable amount, the barium sulphate precipitate may be contaminated with lead sulphate. To correct this, add 5 ml of ammonium acetate solution to the weighe.$ precipitate and digest on steam-bath for 30 minutes. .Filter, wash with hot water and preserve the filtrate for lead determination. Ignite the precipitate and weigh as barium sulphate.

10.4 Calculation

Barium sulphate, percent = $ x 100

where

A = weight in g of barium sulphate, and

B = weight in g of the sample taken.

11. DETERMINATION OF LEAD AS SULPHIDE BY THE GRAVIMETRIC METHOD

II.1 Outline of the Method - In the filtrate obtained after the estimation of barium under 10.3.2 and 10.3.2.1, lead is precipitated as sulphide and then converted to lead sulphate by treating with sulphuric acid. The lead sulphate is ignited and weighed.

11.2 Reagents

11.2.1 Hydrogen Sulphide - gas.

11.2.2 Dilute Hydrochloric Acid - 1 : 1 ( v/v).

11.23 Concentrated Ammonium Hydroxide - 20 percent.

11.2.4 Ammonium Sulphide Wash Solution - Add ?O ml of concentrated ammonium hydroxide to one litre of water cont@ing one gram of tartaric acid and pass hydrogen sulphide gas for about 10 minutes. The solution should contain a slight excess of ammonia, which may be added if required.

112.5 Dilute Nitric Acid - 1 : 1 ( v/v).

15

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IS : 2411 - 1963

11.2.6 Dilute Sulphuric Acid - 1 : 1 ( v/v ).

11.3 Procedure

11.3.1 Pass hydrogen sulphide for a few minutes into the filtrate pre- served under 10.3.2 and 10.3.3, render the solution slightly ammoniacal and add a few drops of dilute hydrochloric acid. Continue to pass hydrogen sulphide for 10 minutes and allow the solution to stand in the steam-bath for 30 minutes. Filter, wa 1 s 1 a few times with ammonium sulphide wash solution and discard the filtrate.

11.3.2 Dissolve the precipitate in 25 ml of hot dilute nitric acid. Dilute the solution and repeat the precipitation and washing in order to eliminate all calcium which might otherwise be precipitated with the lead. Dissolve the precipitate in dilute nitric acid as before, add 3 ml of dilute sulphuric acid and evaporate until dense fumes of acid appear. Cool, dilute with water to 50 ml, add a few drops of rectified spirit and ailow to stand for 3 hours or overnight. Filter through a sintered glass crucible and wash a few times with cold dilute sulphuric acid. Preserve the filtrate for determination of zinc, if any ( see 12). Ignite the preci- pitate very carefully to dull redness in a weighed porcelain crucible.

11.4 Calculation

where

Lead sulphide, percent = -$ x 78.89

A = weight in g of lead sulphate, and

B = weight in g of the sample taken.

12. DETERMINATION OF ZINC AS SULPHIDE BY THE GRAVIMETRIC METHOD

12.1 Outline of the Method - From the filtrate obtained after the esti- mation of lead under 11.3.2, hydroxides of iron and aluminium are removed by making it alkaline with ammonia. Hydrogen sulphide is passed through the cold acid solution for 30 minutes and the precipitate of zinc sulphide thus formed is filtered, ignited and weighed as zinc oxide.

12.2 Reagents - In addition to the reagents required under 9.2, the following reagents are required.

12.2.1 Concentrated Ammonium Hydroxide - 20 percent.

12.2.2 Dilute Sulphuric Acid - 1 : 2 ( v/v).

16

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IS : 2411- 1963

12.2.3 Hydrogen Sulphide - gas.

12.3 Procedure

12.3.1 Remove the oxides of iron and aluminium in the filtrate reserved under 11.3.2 by following the method given under 9.3.1. ( Single preci- pitation for RzO, is enough. ) Carefully neutralize with dilute sulphuric acid and then add enough of dilute sulphuric acid to bring the concentra- tion of acid to about 0.01 N. Cool the solution and pass hydrogen sulphide for 30 minutes. Allow to stand for one hour, filter through a No. 40 filter paper and wash with cold water. Transfer the filter paper along with the precipitate to a weighed porcelain crucible, dry, ignite at a low tempera- ture till all carbon is burnt off and then ignite to 900°C. Weigh as zinc oxide.

12.4 Calculation

where

Zinc sulphide, percent = $ x 1.19

A = weight in g of the ignited residue, and

B = weight in g of the sample taken.

13. DETERMINATION OF SULPHUR BY THE GRAVIMETRIC METHOD

13.1 Outline of the Method - The sample is fused with potassium carbo- nate and potassium nitrate and extracted with water. The extract is evaporated twice with hydrochloric acid to dryness, the dry mass dis- solved in hydrochloric acid and filtered. Sulphur in the filtrate is then precipitated bi barium chloride as barium sulphate.

13.2 Reagents

133.1 Potassium Carbonate - solid.

13.2.2 Potassium Nitrate - solid.

13.2.3 Concentrated Hydrochloric Acid - see 5.2.6.

13.2.4 Dilufe Hydrochhloric Acid - 2 : 98 ( v/v ).

133.5 Barium Chloride Solution - 10 percent ( w/v ).

13.3 Procedure

13.3.1 Mix about two grams of an accurately weighed sample with 10 g of potassium carbonate and @5 g of potassium nitrate. Cover the

17

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IS : 2411 - 1963

crucible and heat in a muffle furnace until the mass is completely fused. When fusion is complete, rotate the crucible gently so that the cooling melt solidifies on the walls in the form of a layer. Place the crucible in a beaker containing 150 ml of warm water. Digest on steam-bath and stir occasionally.

13.3.2 IYhen the melt is disintegrated, filter and wash the residue with small portions of hot water. .4cidify the filtrate with concentrated hydro- chlorlc acid, add 20 to 25 ml in excess. Evaporate to dryness, wash down the inside of the beaker, add again 20 to 25 ml of concentrated hydro- chloric acid and evaporate to dryness. Dissolve the salts in 100 ml of dilute hydrochloric acid. Wash the residue with hot water.

13.3.3 Concentrate the filtrate and adjust the acidity so that it contains 2 percent by volume of hydrochloric acid. Warm it to 60” to 70°C and add IO ml of barium chloride solution dropwise with constant stirring. Let the soiution stand for two hours on steam-bath and overnight at room temperature. Filter through a No. 42 filter paper and wash the precipitate with cold dilute hydrochloric .xid and then with hot water until free from chloride. Dry and ignite the precipitate in a weighed platinum or silica crucible, cool ixr a desiccator and weigh as barium sulphate ( BaSO, ).

13.4 Calcolation

Sulphur, percent = $- x 13.74

where

A = weight in g of barium suiphate obtained under 13.3.3, and

B = weight in g of the sample taken.

18

Page 23: IS 2411 (1963): Methods of chemical analysis of fluorspar ...crucible of fine porosity, avoiding contact with rubber or other organic material. Store in a dark coloured glass bottle.

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