CELEX: 31979L0138
Language: en
Date: 1978-12-14 00:00:00
Title: Commission Directive 79/138/EEC of 14 December 1978 amending Directive 77/535/EEC on the approximation of the laws of the Member States relating to methods of sampling and analysis for fertilizers

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31979L0138

Commission Directive 79/138/EEC of 14 December 1978 amending Directive 77/535/EEC on the approximation of the laws of the Member States relating to methods of sampling and analysis for fertilizers  

Official Journal L 039 , 14/02/1979 P. 0003 - 0010 Finnish special edition: Chapter 13 Volume 9 P. 0150  Greek special edition: Chapter 03 Volume 24 P. 0066  Swedish special edition: Chapter 13 Volume 9 P. 0150  Spanish special edition: Chapter 13 Volume 9 P. 0194  Portuguese special edition Chapter 13 Volume 9 P. 0194 

++++COMMISSION DIRECTIVE  OF 14 DECEMBER 1978  AMENDING DIRECTIVE 77/535/EEC ON THE APPROXIMATION OF THE LAWS OF THE MEMBER STATES RELATING TO METHODS OF SAMPLING AND ANALYSIS FOR FERTILIZERS   ( 79/138/EEC )  THE COMMISSION OF THE EUROPEAN COMMUNITIES ,  HAVING REGARD TO THE TREATY ESTABLISHING THE EUROPEAN ECONOMIC COMMUNITY ,  HAVING REGARD TO COUNCIL DIRECTIVE 76/116/EEC OF 18 DECEMBER 1975 ON THE APPROXIMATION OF THE LAWS OF THE MEMBER STATES RELATING TO FERTILIZERS ( 1 ) , AND IN PARTICULAR ARTICLE 9 ( 2 ) THEREOF ,  WHEREAS COMMISSION DIRECTIVE 77/535/EEC ( 2 ) PROVIDES FOR OFFICIAL CONTROLS FOR EEC FERTILIZERS FOR THE PURPOSE OF CHECKING COMPLIANCE WITH THE REQUIREMENTS IMPOSED BY THE COMMUNITY PROVISIONS CONCERNING THE QUALITY AND COMPOSITION OF FERTILIZERS ; WHEREAS THAT DIRECTIVE SHOULD BE AMENDED BY THE ADDITION OF THREE NEW METHODS OF ANALYSIS ;  WHEREAS THE MEASURES PROVIDED FOR IN THIS DIRECTIVE ARE IN ACCORDANCE WITH THE OPINION OF THE COMMITTEE ON THE ADAPTATION TO TECHNICAL PROGRESS OF THE DIRECTIVES FOR THE REMOVAL OF TECHNICAL BARRIERS TO TRADE IN FERTILIZERS ,  HAS ADOPTED THIS DIRECTIVE :  ARTICLE 1  ANNEX II TO DIRECTIVE 77/535/EEC IS AMENDED BY THE INSERTION AFTER METHOD 5.1 OF METHODS 5.2 , 5.3 AND 5.4 AS ANNEXED TO THIS DIRECTIVE .  ARTICLE 2  1 . THE MEMBER STATES SHALL , NOT LATER THAN 1 APRIL 1979 , BRING INTO FORCE THE LAWS , REGULATIONS OR ADMINISTRATIVE PROVISIONS NECESSARY TO COMPLY WITH THIS DIRECTIVE . THEY SHALL FORTHWITH NOTIFY THE COMMISSION THEREOF .  2 . ONCE NOTIFICATION OF THIS DIRECTIVE HAS BEEN EFFECTED , THE MEMBER STATES SHALL , IN SUFFICIENT TIME TO ENABLE IT TO SUBMIT ITS COMMENTS , INFORM THE COMMISSION OF ALL DRAFT LAWS , REGULATIONS OR ADMINISTRATIVE PROVISIONS WHICH THEY INTEND TO ADOPT IN THE FIELD COVERED BY THIS DIRECTIVE .  ARTICLE 3  THIS DIRECTIVE IS ADDRESSED TO THE MEMBER STATES .  DONE AT BRUSSELS , 14 DECEMBER 1978 .  FOR THE COMMISSION  ETIENNE DAVIGNON  MEMBER OF THE COMMISSION  ( 1 ) OJ NO L 24 , 30 . 1 . 1976 , P . 21 .  ( 2 ) OJ NO L 213 , 22 . 8 . 1977 , P . 1 .  ANNEX  METHOD 5.2  DETERMINATION OF TOTAL MAGNESIUM  1 . SCOPE  THIS DOCUMENT DEFINES THE PROCEDURE FOR THE DETERMINATION OF TOTAL MAGNESIUM .  2 . FIELD OF APPLICATION  EXCLUSIVELY TO THE FERTILIZER MAGNESIUM AMMONIUM NITRATE IN RESPECT OF WHICH ANNEX IA TO COUNCIL DIRECTIVE 76/116/EEC OF 18 DECEMBER 1975 PROVIDES FOR THE INDICATION OF TOTAL MAGNESIUM .  3 . PRINCIPLE  SOLUTION IN BOILING ACID OF THE MAGNESIUM CONTAINED IN A TEST SAMPLE .  FIRST TITRATION WITH EDTA OF CA AND MG IN THE PRESENCE OF ERIOCHROME BLACK-T . SECOND TITRATION WITH EDTA OF CA IN THE PRESENCE OF CALCEIN OR OF CALCON CARBONIC ACID . DETERMINATION OF MAGNESIUM BY DIFFERENCE .  4 . REAGENTS  DISTILLED OR DEMINERALIZED WATER .  4.1 . STANDARD 0,05 MOLAR SOLUTION OF MAGNESIUM .  WEIGH OUT 2,016 G OF MAGNESIUM OXIDE FOR ANALYSIS , PREVIOUSLY CALCINED AT 600 * C FOR TWO HOURS . PLACE IT IN A BEAKER WITH 100 ML OF WATER . STIR IN 120 ML OF APPROXIMATELY 1N HYDROCHLORIC ACID . AFTER DISSOLUTION , TRANSFER QUANTITATIVELY INTO A GRADUATED ONE-LITRE FLASK , MAKE UP THE VOLUME WITH WATER AND MIX .  CHECK THE STRENGTH OF THE SOLUTION GRAVIMETRICALLY AS AMMONIUM-MAGNESIUM PHOSPHATE .  1 ML OF THE SOLUTION SHOULD CONTAIN 1,216 MG OF MG ( = 2,016 MG MGO ) .  4.2 . 0,05 MOLAR SOLUTION OF EDTA  WEIGH OUT 18,61 G OF THE DIHYDRATED DISODIUM SALT OF ETHYLENEDIAMINETETRAACETIC ACID  ( C10H14N2NA2O8 * 2H2O ) , PLACE IT IN A LITRE BEAKER AND DISSOLVE IN 600 TO 800 ML OF WATER . TRANSFER THE SOLUTION QUANTITATIVELY INTO A GRADUATED ONE-LITRE FLASK . MAKE UP THE VOLUME AND MIX . CHECK THIS SOLUTION WITH SOLUTION ( 4.1 ) BY TAKING A SAMPLE OF 20 ML OF THE LATTER AND BY TITRATION ACCORDING TO ANALYTICAL PROCEDURE 7.4.1 .  1 ML OF THE EDTA SOLUTION SHOULD CORRESPOND TO 1,216 MG OF MG OR 2,016 MG OF MGO AND TO 2,004 MG OF CA OR 2,804 MG OF CAO ( SEE REMARKS 9.1 AND 9.6 ) .  4.3 . 0,05 MOLAR STANDARD SOLUTION OF CALCIUM  WEIGH OUT 5,004 G OF DRY PURE CALCIUM CARBONATE . PLACE IT IN A BEAKER WITH 100 ML OF WATER . PROGRESSIVELY STIR IN 120 ML OF APPROXIMATELY 1N HYDROCHLORIC ACID .  BRING TO THE BOIL IN ORDER TO DRIVE OFF THE CARBON DIOXIDE , COOL , TRANSFER QUANTITATIVELY INTO A GRADUATED ONE-LITRE FLASK , MAKE UP THE VOLUME WITH WATER AND MIX . CHECK THIS SOLUTION AGAINST THE EDTA SOLUTION ( 4.2 ) FOLLOWING ANALYTICAL PROCEDURE 7.4.2 . 1 ML OF THIS SOLUTION SHOULD CONTAIN 2,004 MG OF CA ( = 2,804 MG OF CAO ) AND SHOULD CORRESPOND TO 1 ML OF THE 0,05 MOLAR EDTA SOLUTION .  4.4 . CALCEIN INDICATOR  CAREFULLY MIX IN A MORTAR 1 G OF CALCEIN WITH 100 G OF SODIUM CHLORIDE . USE 10 MG OF THIS MIXTURE . THE INDICATOR CHANGES FROM GREEN TO ORANGE . TITRATION MUST BE CARRIED OUT UNTIL AN ORANGE COLOUR IS OBTAINED WHICH IS FREE FROM GREEN TINGES .  4.5 . CALCON CARBONIC ACID INDICATOR  DISSOLVE 400 MG OF CALCON CARBONIC ACID IN 100 ML OF METHANOL . USE THREE DROPS OF THIS SOLUTION . THIS INDICATOR TURNS FROM RED TO BLUE AND TITRATION MUST BE CARRIED OUT UNTIL A BLUE COLOUR IS OBTAINED WHICH IS FREE FROM RED TINGES .  4.6 . ERIOCHROME BLACK-T INDICATOR  DISSOLVE 300 MG ERIOCHROME BALCK-T IN A MIXTURE OF 25 ML PROPANOL-1 AND 15 ML TRIETHANOLAMINE . USE THREE DROPS OF THIS SOLUTION . THIS INDICATOR TURNS FROM RED TO BLUE AND TITRATION MUST BE CARRIED OUT UNTIL A BLUE COLOUR IS OBTAINED WHICH IS FREE FROM RED TINGES . IT CHANGES COLOUR ONLY WHEN MAGNESIUM IS PRESENT . IF NECESSARY ADD 0,1 ML OF STANDARD SOLUTION 4.1 . WHEN BOTH CALCIUM AND MAGNESIUM ARE PRESENT THE EDTA FIRST FORMS A COMPLEX WITH THE CALCIUM AND THEN WITH THE MAGNESIUM . IN THAT CASE THESE TWO ELEMENTS ARE DETERMINED CONCURRENTLY .  4.7 . POTASSIUM CYANIDE  AQUEOUS SOLUTION OF KCN AT 2 % .  4.8 . SOLUTION OF POTASSIUM HYDROXIDE AND POTASSIUM CYANIDE .  DISSOLVE 280 G OF KOH AND 66 G OF KCN IN WATER , MAKE UP THE VOLUME TO ONE LITRE AND MIX .  4.9 . PH 10,5 BUFFER SOLUTION  DISSOLVE 33 G OF AMMONIUM CHLORIDE IN 200 ML OF WATER , ADD 250 ML OF AMMONIA ( D = 0,91 ) MAKE UP THE VOLUME TO 500 ML WITH WATER AND MIX . TEST THE PH OF THIS SOLUTION REGULARLY .  4.10 . DILUTED HYDROCHLORIC ACID 1 : 1  ONE PART OF HYDROCHLORIC ACID ( 1,18 DENSITY ) AND ONE PART OF WATER .  4.11 . SODIUM HYDROXIDE SOLUTION 5N  5 . APPARATUS  5.1 . MAGNETIC OR MECHANICAL STIRRER .  5.2 . PH METER .  5.3 . GRADUATED 500 ML AND 1 000 ML FLASKS .  5.4 . 300 ML BEAKERS .  6 . PREPARATION OF THE SAMPLE  SEE METHOD 1 .  7 . PROCEDURE  7.1 . SAMPLE  PLACE 5 G OF THE PREPARED SAMPLE WEIGHED OUT TO AN ACCURACY OF 1 MG IN A GRADUATED 500 ML FLASK .  7.2 . SOLUTION  ADD ABOUT 200 ML WATER AND 20 ML HYDROCHLORIC ACID  ( 4.10 ) , BOIL FOR HALF AN HOUR . COOL , MAKE UP THE VOLUME WITH WATER , MIX AND FILTER .  7.3 . CONTROL TEST  CARRY OUT A DETERMINATION ON ALIQUOT PARTS OF SOLUTIONS  ( 4.1 ) AND ( 4.3 ) SUCH THAT THE CA/MG RATIO IS EQUAL TO THAT EXPECTED FROM THE SAMPLE .  TO THIS END TAKE ( A ) ML OF STANDARD SOLUTION  ( 4.3 ) AND ( B - A ) ML STANDARD SOLUTION ( 4.1 ) .   ( A ) AND ( B ) ARE THE NUMBERS OF ML EDTA SOLUTION USED IN THE TWO TITRATIONS WHEN ANALYZING THE SAMPLE . THIS PROCEDURE IS CORRECT ONLY IF THE STANDARD SOLUTIONS OF EDTA , CALCIUM AND MAGNESIUM ARE EXACTLY EQUIVALENT . IF THIS IS NOT THE CASE , IT IS NECESSARY TO MAKE THE APPROPRIATE CORRECTIONS .  7.4 . DETERMINATION  7.4.1 . TITRATION IN THE PRESENCE OF ERIOCHROME BLACK-T  PIPETTE 50 ML ( 1 ) OF THE SOLUTION TO BE ANALYZED INTO A 300 ML BEAKER . NEUTRALIZE THE SURPLUS ACID WITH THE 5N SODIUM HYDROXIDE SOLUTION ( 4.11 ) USING THE PH METER . DILUTE WITH WATER TO 100 ML . ADD 5 ML OF THE BUFFER SOLUTION ( 4.9 ) . THE PH MEASURED BY THE METER MUST BE 10,5 + 0,1 . ADD 2 ML OF THE POTASSIUM CYANIDE SOLUTION ( 4.7 ) AND THREE DROPS OF THE ERIOCHROME BLACK-T INDICATOR ( 4.6 ) . TITRATE WITH THE EDTA SOLUTION ( 4.2 ) , STIRRING GENTLY WITH THE STIRRER ( 5.1 ) . ( SEE 9.2 , 9.3 AND 9.4 ) . LET " B " BE THE NUMBER OF ML OF 0,05 MOLAR EDTA SOLUTION .  7.4.2 . TITRATION IN THE PRESENCE OF CALCEIN OR OF CALCON CARBONIC ACID  PIPETTE AN ALIQUOT PART OF THE SOLUTION TO BE ANALYZED EQUAL TO THAT TAKEN FOR THE ABOVE TITRATION AND PLACE IT IN A 300 ML BEAKER . NEUTRALIZE THE SURPLUS ACID WITH THE 5N SODIUM HYDROXIDE SOLUTION  ( 4.11 ) USING THE PH METER . DILUTE WITH WATER TO ABOUT 100 ML . ADD 10 ML OF THE KOH/KCN SOLUTION ( 4.8 ) AND THE INDICATOR ( 4.4 ) OR ( 4.5 ) . STIR GENTLY AND TITRATE WITH THE EDTA SOLUTION . ( SEE NOTES 9.2 , 9.3 AND 9.4 . ) LET " A " BE THE NUMBER OF ML OF 0,05 MOLAR EDTA SOLUTION .  8 . EXPRESSION OF THE RESULT  THE RESULT IS EXPRESSED AS A PERCENTAGE OF MGO OR MG  8.1 . % MGO IN THE FERTILIZER = ( B - A ) BY T/M  OR   % MG IN THE FERTILIZER = ( B - A ) BY T'/M  IF THE STRENGTH OF EDTA SOLUTION IS EXACTLY 0,05 M , T = 0,2016 AND T MG = 0,1216 .  M = THE WEIGHT OF THE SAMPLE , EXPRESSED IN GRAMS , PRESENT IN THE ALIQUOT TAKEN AS A SAMPLE .  9 . REMARKS  SEE METHOD 5.1 .  ( 1 ) AT THE TIME OF TITRATION 25 ML EDTA SHOULD NOT BE GREATLY EXCEEDED AS OTHERWISE THE VOLUME OF THE ALIQUOT PART MUST BE REDUCED . HOWEVER , IT MAY ALSO BE INCREASED .  METHOD 5.3  DETERMINATION OF WATER SOLUBLE MAGNESIUM  1 . SCOPE  THIS DOCUMENT DEFINES THE PROCEDURE FOR THE DETERMINATION OF WATER SOLUBLE MAGNESIUM .  2 . FIELD OF APPLICATION  EXCLUSIVELY TO FERTILIZERS IN RESPECT OF WHICH ANNEX IA TO DIRECTIVE 76/116/EEC PROVIDES FOR THE DECLARATION OF WATER SOLUBLE MAGNESIUM .  3 . PRINCIPLE  A SOLUTION OF MAGNESIUM IS OBTAINED BY BOILING THE TEST SAMPLE IN WATER , AND THE MAGNESIUM IS DETERMINED BY ATOMIC ABSORPTION SPECTROPHOTOMETRY .  4 . REAGENTS  DISTILLED WATER OR DEMINERALIZED WATER OF EQUIVALENT QUALITY .  4.1 . HYDROCHLORIC ACID , 1N SOLUTION ( APPROXIMATELY )  4.2 . HYDROCHLORIC ACID , 0,5N SOLUTION  4.3 . MAGNESIUM STANDARD SOLUTION : DISSOLVE 1,013 G MAGNESIUM SULPHATE ( MGSO4 * 7H2O ) FOR ANALYSIS IN 0,5N HYDROCHLORIC ACID SOLUTION ( 4.2 ) AND DILUTE TO 100 ML WITH THE SAME ACID .  1 ML OF THIS SOLUTION CONTAINS 1 MG OF MAGNESIUM ( MG ) .  OR  WEIGH OUT 1,658 G OF MAGNESIUM OXIDE , FOR ANALYSIS , PREVIOUSLY CALCINED AT 600 * C FOR TWO HOURS . PLACE IT IN A BEAKER WITH 100 ML OF WATER AND 120 ML OF APPROXIMATELY 1N HYDROCHLORIC ACID ( 4.1 ) . AFTER DISSOLUTION , TRANSFER QUANTITATIVELY INTO A ONE-LITRE GRADUATED FLASK , MAKE UP THE VOLUME WITH WATER AND MIX .  1 ML OF THIS SOLUTION CONTAINS 1 MG OF MAGNESIUM ( MG ) .  4.4 . STRONTIUM CHLORIDE SOLUTION : DISSOLVE 75 G STRONTIUM CHLORIDE ( SRCL2 * 6H2O ) IN 0,5N HYDROCHLORIC ACID SOLUTION ( 4.2 ) AND DILUTE TO 500 ML WITH THE SAME SOLVENT .  5 . APPARATUS  5.1 . ATOMIC ABSORPTION SPECTROPHOTOMETER WITH A MAGNESIUM LAMP ( 285,2 NM ) .  5.2 . PRECISION PIPETTES 5 , 10 , 20 , 25 AND 30 ML .  5.3 . GRADUATED FLASKS 100 , 200 , 500 AND 1 000 ML .  6 . PREPARATION OF SAMPLE  SEE METHOD 1 .  7 . PROCEDURE  7.1 . SAMPLE   ( PLACE 5 G OF SAMPLE , WEIGHED TO THE NEAREST 0,001 G INTO A GRADUATED 500 ML FLASK .  7.2 . SOLUTION   ( ADD ABOUT 300 ML WATER , AND BOIL THE RESULTING SOLUTION FOR HALF AN HOUR . ALLOW TO COOL , DILUTE TO THE MARK WITH WATER , MIX AND FILTER .  7.3 . PREPARATION OF THE SAMPLE SOLUTION  7.3.1 . IF THE FERTILIZER HAS A DECLARED MAGNESIUM CONTENT ( MGO ) GREATER THAN 10 % , DILUTE BY PRECISION PIPETTE 25 ML OF THE FILTRATE  ( 7.2 ) TO 100 ML IN A 100 ML GRADUATED FLASK , MAKE UP TO THE MARK WITH WATER AND MIX .  7.3.2 . TRANSFER BY PRECISION PIPETTE 10 ML OF THE FILTRATE ( 7.2 ) OR THE DILUTED FILTRATE  ( 7.3.1 ) , INTO A 200 ML GRADUATED FLASK AND MAKE UP TO THE MARK WITH 0,5N HYDROCHLORIC ACID SOLUTION  ( 4.2 ) .  7.3.3 . DILUTE THE SOLUTION ( 7.3.2 ) WITH 0,5N HYDROCHLORIC ACID SOLUTION ( 4.2 ) TO A CONCENTRATION SITUATED INSIDE THE WORKING RANGE OF THE SPECTROPHOTOMETER . THE FINAL SOLUTION MUST CONTAIN 10 % V/V OF STRONTIUM CHLORIDE SOLUTION ( 4.4 ) .  7.4 . PREPARATION OF BLANK SOLUTION  PREPARE A BLANK SOLUTION FROM WHICH ONLY THE SAMPLE HAS BEEN OMITTED .  7.5 . PREPARATION OF STANDARD SOLUTIONS FOR CALIBRATION  BY DILUTING THE STANDARD SOLUTION ( 4.3 ) WITH 0,5N HYDROCHLORIC ACID SOLUTION ( 4.2 ) PREPARE AT LEAST FIVE REFERENCE SOLUTIONS OF INCREASING CONCENTRATION CORRESPONDING TO THE OPTIMAL MEASURING RANGE OF THE SPECTROPHOTOMETER .  THE FINAL SOLUTIONS MUST CONTAIN 10 % V/V STRONTIUM CHLORIDE SOLUTION ( 4.4 ) .  7.6 . MEASUREMENT  SET UP THE SPECTROPHOTOMETER ( 5.1 ) , AT A WAVELENGTH OF 285,2 NM . SPRAY SUCCESSIVELY , IN TRIPLICATE , THE STANDARD SOLUTIONS ( 7.5 ) , THE SAMPLE SOLUTION ( 7.3 ) AND THE BLANK SOLUTION ( 7.4 ) , WASHING THE INSTRUMENT THROUGH WITH DISTILLED WATER BETWEEN EACH SPRAYING . PLOT THE CALIBRATION CURVE USING THE MEAN ABSORBANCES AS THE ORDINATES AND THE CORRESPONDING CONCENTRATION OF MAGNESIUM IN MG/ML AS THE ABSCISSAE . DETERMINE THE CONCENTRATION OF MAGNESIUM IN THE SAMPLE AND BLANK BY REFERENCE TO THE CALIBRATION CURVE .  8 . CALCULATION OF RESULTS  CALCULATE THE QUANTITY OF MAGNESIUM ( MG ) OR MAGNESIUM OXIDE ( MGO ) , CONVERSION FACTOR 1,66 , IN THE SAMPLE BY RELATION TO THE REFERENCE SOLUTIONS , AND TAKING INTO CONSIDERATION THE BLANK . EXPRESS THE RESULT AS A PERCENTAGE OF THE SAMPLE .  METHOD 5.4  DETERMINATION OF TOTAL MAGNESIUM  1 . SCOPE  THIS DOCUMENT DEFINES THE PROCEDURE FOR THE DETERMINATION OF TOTAL MAGNESIUM .  2 . FIELD OF APPLICATION  EXCLUSIVELY TO THE FERTILIZER MAGNESIUM AMMONIUM NITRATE IN RESPECT OF WHICH ANNEX IA TO DIRECTIVE 76/116/EEC PROVIDES FOR THE DECLARATION OF TOTAL MAGNESIUM .  3 . PRINCIPLE  A SOLUTION OF MAGNESIUM IS OBTAINED BY BOILING THE TEST SAMPLE IN DILUTE ACID , AND THE MAGNESIUM IS DETERMINED BY ATOMIC ABSORPTION SPECTROPHOTOMETRY .  4 . REAGENTS  DISTILLED WATER OR DEMINERALIZED WATER OF EQUIVALENT QUALITY .  4.1 . HYDROCHLORIC ACID SOLUTION ( 1 : 1 ) : DILUTE ONE VOLUME OF HYDROCHLORIC ACID ( D = 1,18 ) WITH ONE VOLUME OF WATER .  4.2 . HYDROCHLORIC ACID , 1N SOLUTION ( APPROXIMATELY )  4.3 . HYDROCHLORIC ACID , 0,5N SOLUTION .  4.4 . MAGNESIUM STANDARD SOLUTION : DISSOLVE 1,013 G MAGNESIUM SULPHATE ( MGSO4 * 7H2O ) FOR ANALYSIS IN 0,5N HYDROCHLORIC SOLUTION ( 4.3 )  AND DILUTE TO 100 ML WITH THE SAME ACID .  1 ML OF THIS SOLUTION CONTAINS 1 MG OF MAGNESIUM  ( MG ) .  OR  WEIGH OUT 1,658 G OF MAGNESIUM OXIDE , PREVIOUSLY CALCINED AT 600 * C FOR TWO HOURS . PLACE IT IN A BEAKER WITH 100 ML OF WATER AND 120 ML OF APPROXIMATELY 1N HYDROCHLORIC ACID ( 4.2 ) . AFTER DISSOLUTION , TRANSFER QUANTITATIVELY INTO A ONE LITRE GRADUATED FLASK , MAKE UP THE VOLUME WITH WATER AND MIX .  1 ML OF THIS SOLUTION CONTAINS 1 MG OF MAGNESIUM ( MG ) .  4.5 . STRONTIUM CHLORIDE SOLUTION : DISSOLVE 75 G STRONTIUM CHLORIDE ( SRCL2 * 6H2O ) IN 0,5N HYDROCHLORIC ACID SOLUTION ( 4.3 ) AND DILUTE TO 500 ML WITH THE SAME SOLVENT .  5 . APPARATUS  5.1 . ATOMIC ABSORPTION SPECTROPHOTOMETER WITH A MAGNESIUM LAMP ( 285,2 NM ) .  5.2 . PRECISION PIPETTES 5 , 10 , 20 , 25 AND 30 ML .  5.3 . GRADUATED FLASK 100 , 200 , 500 AND 1 000 ML .  6 . PREPARATION OF SAMPLE  SEE METHOD 1 .  7 . PROCEDURE  7.1 . SAMPLE  PLACE 5 G OF SAMPLE , WEIGHED TO THE NEAREST 0,001 G INTO A GRADUATED 500 ML FLASK .  7.2 . SOLUTION  ADD ABOUT 200 ML WATER , 20 ML OF HYDROCHLORIC ACID SOLUTION ( 4.1 ) AND BOIL THE RESULTING SOLUTION FOR HALF AN HOUR . ALLOW TO COOL , DILUTE TO THE MARK WITH WATER , MIX AND FILTER .  7.3 . PREPARATION OF THE SAMPLE SOLUTION  7.3.1 . IF THE FERTILIZER HAS A DECLARED MAGNESIUM CONTENT ( MGO ) GREATER THAN 10 % , DILUTE BY PRECISION PIPETTE 25 ML OF THE FILTRATE ( 7.2 ) TO 100 ML IN A 100 ML GRADUATED FLASK , MAKE UP TO THE MARK WITH WATER AND MIX .  7.3.2 . TRANSFER BY PRECISION PIPETTE 10 ML OF THE FILTRATE ( 7.2 ) OR THE DILUTED FILTRATE ( 7.3.1 ) , INTO A 200 ML GRADUATED FLASK AND MAKE UP TO THE MARK WITH 0,5N HYDROCHLORIC ACID SOLUTION ( 4.3 ) .  7.3.3 . DILUTE THIS SOLUTION ( 7.3.2 ) WITH 0,5N HYDROCHLORIC ACID SOLUTION ( 4.3 ) TO A CONCENTRATION SITUATED INSIDE THE WORKING RANGE OF THE SPECTROPHOTOMETER .  THE FINAL SOLUTION MUST CONTAIN 10 % V/V STRONTIUM CHLORIDE SOLUTION ( 4.5 ) .  7.4 . PREPARATION OF BLANK SOLUTION  PREPARE A BLANK SOLUTION FROM WHICH ONLY THE SAMPLE HAS BEEN OMITTED .  7.5 . PREPARATION OF STANDARD SOLUTION FOR CALIBRATION  BY DILUTING THE STANDARD SOLUTION ( 4.4 ) WITH 0,5N HYDROCHLORIC ACID SOLUTION ( 4.3 ) PREPARE AT LEAST FIVE REFERENCE SOLUTIONS OF INCREASING CONCENTRATION CORRESPONDING TO THE OPTIMAL MEASURING RANGE OF THE SPECTROPHOTOMETER .  THE FINAL SOLUTIONS MUST CONTAIN 10 % V/V STRONTIUM CHLORIDE SOLUTION ( 4.5 ) .  7.6 . MEASUREMENT  SET UP THE SPECTROPHOTOMETER ( 5.1 ) , AT A WAVELENGTH OF 285,2 NM . SPRAY SUCCESSIVELY , IN TRIPLICATE , THE STANDARD SOLUTION ( 7.5 ) , THE SAMPLE SOLUTION ( 7.3 ) AND THE BLANK SOLUTION  ( 7.4 ) , WASHING THE INSTRUMENT THROUGH WITH DISTILLED WATER BETWEEN EACH SPRAYING . PLOT THE CALIBRATION CURVE USING THE MEAN ABSORBANCES AS THE ORDINATES AND THE CORRESPONDING CONCENTRATIONS OF MAGNESIUM IN MG/ML AS THE ABSCISSAE . DETERMINE THE CONCENTRATION OF MAGNESIUM IN THE SAMPLE AND BLANK BY REFERENCE TO THE CALIBRATION CURVE .  8 . CALCULATION OF RESULTS  CALCULATE THE QUANTITY OF MAGNESIUM ( MG ) OR MAGNESIUM OXIDE ( MGO ) ( CONVERSION FACTOR 1,66 ) IN THE SAMPLE BY RELATION TO THE REFERENCE SOLUTIONS , AND TAKING INTO CONSIDERATION THE BLANK . EXPRESS THE RESULT AS A PERCENTAGE OF THE SAMPLE .