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    BS EN 13806-2002 Foodstuffs - Determination of trace elements - Determination of mercury by cold-vapour atomic absorption spectrometry (CVAAS) after pressure digestion《鞋袜 痕量元素的测定 加.pdf

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    BS EN 13806-2002 Foodstuffs - Determination of trace elements - Determination of mercury by cold-vapour atomic absorption spectrometry (CVAAS) after pressure digestion《鞋袜 痕量元素的测定 加.pdf

    1、BRITISH STANDARD BS EN 13806:2002 Foodstuffs Determination of trace elements Determination of mercury by cold-vapour atomic absorption spectrometry (CVAAS) after pressure digestion The European Standard EN 13806:2002 has the status of a British Standard ICS 67.050 BS EN 13806:2002 This British Stand

    2、ard, having been prepared under the direction of the Consumer Products and Services Sector Policy and Strategy Committee, was published under the authority of the Standards Policy and Strategy Committee on 10 September 2002 BSI 10 September 2002 ISBN 0 580 40367 X National foreword This British Stan

    3、dard is the official English language version of EN 13806:2002 The UK participation in its preparation was entrusted to Technical Committee AW/-/3, Horizontal analysis, which has the responsibility to: A list of organizations represented on this committee can be obtained on request to its secretary.

    4、 Cross-references The British Standards which implement international or European publications referred to in this document may be found in the BSI Catalogue under the section entitled “International Standards Correspondence Index”, or by using the “Search” facility of the BSI Electronic Catalogue o

    5、r of British Standards Online. This publication does not purport to include all the necessary provisions of a contract. Users are responsible for its correct application. Compliance with a British Standard does not of itself confer immunity from legal obligations. aid enquirers to understand the tex

    6、t; present to the responsible international/European committee any enquiries on the interpretation, or proposals for change, and keep the UK interests informed; monitor related international and European developments and promulgate them in the UK. Summary of pages This document comprises a front cov

    7、er, an inside front cover, the EN title page, pages 2 to 11 and a back cover. The BSI copyright date displayed in this document indicates when the document was last issued. Amendments issued since publication Amd. No. Date CommentsEUROPEANSTANDARD NORMEEUROPENNE EUROPISCHENORM EN13806 August2002 ICS

    8、67.050 Englishversion FoodstuffsDeterminationoftraceelementsDeterminationof mercurybycoldvapouratomicabsorptionspectrometry (CVAAS)afterpressuredigestion ProduitsalimentairesDosagedeslmentstraces Dosagedumercureparspectromtriedabsorption atomiquepargnrationdevapeursfroidesaprsdigestion souspression

    9、LebensmittelBestimmungvonElementspuren BestimmungvonQuecksilbermit Atomabsorptionsspektrometrie(AAS)Kaltdampftechnik nachDruckaufschluss ThisEuropeanStandardwasapprovedbyCENon29May2002. CENmembersareboundtocomplywiththeCEN/CENELECInternalRegulationswhichstipulatetheconditionsforgivingthisEurope an S

    10、tandardthestatusofanationalstandardwithoutanyalteration.Uptodatelistsandbibliographicalreferencesconcernings uchnational standardsmaybeobtainedonapplicationtotheManagementCentreortoanyCENmember. ThisEuropeanStandardexistsinthreeofficialversions(English,French,German).Aversioninanyotherlanguagemadeby

    11、tra nslation undertheresponsibilityofaCENmemberintoitsownlanguageandnotifiedtotheManagementCentrehasthesamestatusasthe official versions. CENmembersarethenationalstandardsbodiesofAustria,Belgium,CzechRepublic,Denmark,Finland,France,Germany,Greece, Iceland,Ireland,Italy,Luxembourg,Malta,Netherlands,N

    12、orway,Portugal,Spain,Sweden,SwitzerlandandUnitedKingdom. EUROPEANCOMMITTEEFORSTANDARDIZATION COMITEUROPENDENORMALISATION EUROPISCHESKOMITEEFRNORMUNG ManagementCentre:ruedeStassart,36B1050Brussels 2002CEN Allrightsofexploitationinanyformandbyanymeansreserved worldwideforCENnationalMembers. Ref.No.EN1

    13、3806:2002EEN13806:2002(E) 2 Contents page Foreword3 1 Scope 3 2 Normativereferences 3 3 Principle3 4 Reagents.4 5 Apparatusandequipment. 5 6 Procedure .5 7 Calculation6 8 Limitofquantification . 6 9 Precision.7 10 Testreport 8 AnnexA (informative) Resultsoftheinterlaboratorytests .9 Bibliography 11E

    14、N13806:2002(E) 3 Foreword ThisEuropeanStandardhasbeenpreparedbyTechnicalCommitteeCEN/TC275“FoodanalysisHorizontal methods“,thesecretariatofwhichisheldbyDIN. ThisEuropeanStandardshallbegiventhestatusofanationalstandard,eitherbypublicationofanidenticaltextor byendorsement,atthelatestbyFebruary2003,and

    15、conflictingnationalstandardsshallbewithdrawnatthelatest byFebruary2003. AnnexAisinformative. AccordingtotheCEN/CENELECInternalRegulations,thenationalstandardsorganizationsofthefollowingcoun triesareboundtoimplementthisEuropeanStandard:Austria,Belgium,CzechRepublic,Denmark,Finland, France,Germany,Gre

    16、ece,Iceland,Ireland,Italy,Luxembourg,Malta,Netherlands,Norway,Portugal,Spain,Swe den,SwitzerlandandtheUnitedKingdom. 1Scope ThisEuropeanStandardspecifiesamethodforthedeterminationofmercuryinfoodstuffsbycoldvapouratomic absorptionspectrometry(CVAAS)afterpressuredigestion. SpecificfoodstuffsforwhichEu

    17、ropeanStandardsexistareexcludedfromthescopeofthishorizontalEuropean Standard.Itisthetaskoftheanalysttoreviewifverticalstandardsexist. 2 Normativereferences ThisEuropeanStandardincorporatesbydatedorundatedreference,provisionsfromotherpublications.These normativereferencesarecitedattheappropriateplace

    18、sinthetext,andthepublicationsarelistedhereafter.For datedreferences,subsequentamendmentstoorrevisionsofanyofthesepublicationsapplytothisEuropean Standardonlywhenincorporatedinitbyamendmentorrevision.Forundatedreferencesthelatesteditionofthe publicationreferredtoapplies(includingamendments). EN13804,

    19、FoodstuffsDeterminationoftraceelements Performancecriteria,generalconsiderationsand samplepreparation. EN13805, FoodstuffsDeterminationoftraceelementsPressuredigestion. 3Principle Determinationofmercuryinthetestsolutionbycoldvapouratomicabsorptionspectrometry(CVAAS)afterpressure digestionaccordingto

    20、EN13805. Thetestsolutionistransferredtothereactionvesselofthemercuryanalysisunit,andthemercuryisreducedwith divalenttinorsodiumborohydrideandflushedintothecuvetteoftheAASinstrumentusingacarriergasstream. Theabsorptionat253,7nm(mercuryline)isusedasameasureofthemercuryconcentrationinthecuvette.Ifthe a

    21、mountsofmercuryinthetestsolutionareverysmall,itisadvisabletoenrichthemercuryexpelledona gold/platinumgauze(amalgamtechnique)priortodeterminationinthecuvette.EN13806:2002(E) 4 WARNINGTheuseofthisstandardcaninvolvehazardousmaterials,operationsandequipment.This standarddoesnotpurporttoaddressallthesafe

    22、typroblemsassociatedwithitsuse.Itistheresponsibility oftheuserofthisstandardtoestablishappropriatesafetyandhealthpracticesanddeterminetheapplica bilityofregulatorylimitationspriortouse. 4Reagents 4.1General Theconcentrationofthetraceelementsinthereagentsandwaterusedshallbelowenoughnottoaffectthere s

    23、ultsofthedetermination. 4.2Hydrochloricacid, notlessthan30%(massfraction),ofapproximately (HCl)=1,15g/ml. 4.3Nitricacid, notlessthan65%(massfraction),ofapproximately (HNO 3 )=1,4g/ml. 4.4Dilutednitricacid. Mixnitricacid(4.3)andwaterinaproportionof1+9partsbyvolumeasaminimum. 4.5Reducingagent 4.5.1Gen

    24、eral Tin(II)chlorideorsodiumborohydridemaybeusedasthereducingagent,butitisnotadvisabletousethetwo reagentsalternately.Observetheinstructionsofthemanufacturersoftheapparatus. 4.5.2 Tin(II)chloridesolution withaconcentrationof100g/l. Dissolve50goftin(II)chloride,SnCl 2 2H 2 Oinapproximately100mlofhydr

    25、ochloricacid(4.2)ina500mlvolu metricflaskanddilutetothemarkwithwater.Prepareafreshsolution. 4.5.3 Sodiumborohydridesolution withaconcentrationof30g/l. Dissolve3gofsodiumborohydridetogetherwith1gofsodiumhydroxidepelletsinwateranddiluteto100ml. Prepareafreshsolutiondailyand,whennecessary,filteritbefor

    26、euse. Theconcentrationbymassofthereducingagentsolutionsmaybevariedtosuitthesystemandtherelevantinfor mationprovidedbythemanufactureroftheapparatusshallbeobserved. WARNINGItisessentialtoobservethe safetyinstructions for working with sodium borohydride. So diumborohydrideformshydrogenwithacidsandthisc

    27、anresultinanexplosiveair/hydrogenmixture.A permanentextractionsystemshallbeprovidedatthepointwheremeasurementsarecarriedout. 4.6Potassiumpermanganatesolution withaconcentrationof40g/l. Dissolve0,4gofpotassiumpermanganatesolutioninwateranddiluteto10ml.Prepareafreshsolutiondaily. 4.7Potassiumdichromat

    28、esolution withaconcentrationof5g/l. Dissolve5gofpotassiumdichromatein500mlofnitricacid(4.3)anddiluteto1lwithwater.EN13806:2002(E) 5 4.8Mercurystocksolution withamercuryconcentrationof1000mg/l. Dissolve1,080gofmercury(II)oxidein10mlofpotassiumdichromatesolution(4.7)anddiluteto1lwithwater. Thestocksol

    29、utionisalsocommerciallyavailable.Itisadvisabletousecertifiedstocksolutions. 4.9Mercurycalibrationsolutions. Dilutethestocksolutionstotheconcentrationsneededforcalibration,with10mlofpotassiumdichromatesolution (4.7)perlitreineachsolution.Choosetheconcentrationssoasnottoexceedthelinearrangeofthecalibr

    30、ation function.Itisrecommendedtouseaminimumof3calibrationsolutionswithdifferentconcentrations. Theconcentrationofacidinthecalibrationsolutionsshallbeequaltothatinthetestsolution.Mercurysolutionsare notstableforalongtime,evenatfairlyhighconcentrationsandshallthereforebemadeupdaily. 4.10 Zeromembercom

    31、pensationsolution. Thezeromembercompensationsolutionshallcontainwater,10ml/lofpotassiumdichromate(4.7)andanamount ofnitricacid(4.3)whichisequaltotheacidconcentrationinthetestsolution. 5 Apparatusandequipment 5.1General Tominimisethecontamination,allapparatuswhichcomeintodirectcontactwiththesampleand

    32、thesolutions shouldbecarefullypretreatedaccordingtoEN13804. 5.2Atomicabsorptionspectrometer, optionallywithbackgroundcorrection,andwiththeaccessoriesused forthecoldvapourandoptionallyamalgamtechniquesandwithameasurementandrecordingsystem.Asanal ternativetothemanualmethod,aflowinjectionsystemmaybeuse

    33、d. 5.3Elementspecificlamp formercury. 6Procedure 6.1Coldvapouratomicabsorptionspectrometry(CVAAS) 6.1.1Spectrometer settings Todeviseatestschedule,firstadjusttheapparatusasspecifiedintheoperatingmanualofthemanufacturer,then optimisethesettings,payingparticularattentiontogasflowtimesandtheamountsofti

    34、n(II)chlorideorsodium borohydrideintroduced. 6.1.2 ExampleofCVAASdetermination Adjustthezerooftheinstrumentusingthezeromembercompensationsolutiondescribedin4.10whennecessary. Usetheappropriatecalibrationsolutionstoobtainthecalibrationfunction.Ifpossible,calibratethemeasurement readingdirectlyinconce

    35、ntrationusingthecalibrationsolutions.Checkthelinearrangeofthecalibrationfunction regularly. Afterthecalibrationfunctionhasbeenestablished,thetestsolutionmaybeusedforthedetermination,eitherwith outfurthertreatmentor,iftheconcentrationisoutsidethelinearrange,aftersuitabledilution.Whencarryingout prolo

    36、ngedseriesofmeasurements,itisadvisabletocheckthezeroandthecalibrationatintervals.EN13806:2002(E) 6 Inordertoavoidabsorptionofmercuryonthewallsofthemeasuringvesselsandtoenhancestabilityofcalibration andsamplesolutionsduringlongruns,itmaybeadvisabletoaddafewdropsofpotassiumpermanganatesolution (4.6)to

    37、thesamplesolutioninthemeasuringvesseluntiltheredcolorationispermanent.Allowthesolutionto standfortenminutesbeforeconnectingittothereactionunitforthedetermination. Althoughacorrectionisseldomnecessaryinthecaseofthecoldvapourtechnique,whetherthebackgroundcor rectionisnecessaryornotshallbecheckedforeve

    38、rytypeofsample.Asananalyticalqualitycontrol,reference sampleshavingreliablyknownmercurycontentsshallbeanalysedinparallelwithalltheseriesofsamplesana lysed,thereferencesamplesbeingsubjectedtoallthestepsinthemethodstartingfromdigestion.Blanksolutions preparedbysubjectingthemtoallthestepsinthemethodsha

    39、llalsobedetermined. 7Calculation Calculatethemassfractionofmercury, w,inmilligramsperkilogramofsample,usingthefollowingequation: 1000 1 = m V V a w (1) where a istheabsolutemassofmercury,innanogram,foundinthetestsolutionused; V isthevolumeofthedigestionsolutionafterbeingmadeup,inmillilitre; V 1 isth

    40、evolumeoftestsolutionused,inmillilitre; m istheinitialsamplemass,ingram. Ifnecessary,subtracttheresultoftheblanksolutionfromthecontent, a,ofmercury. 8 Limitofquantification ThelimitofquantificationaccordingtoEN13804ofthemeasuringsolutiondependsonthefollowingparameters: principleofreleaseofmercury(ba

    41、tchorflowsystem); enrichment(amalgam)ornoenrichment; inthecaseofflowsystems: continuous/discontinuousreleaseofHg; amountofdigestionsolutionused; constructionoftheequipment; influencesofthematrix. Thelimitofquantificationisregularlyintherangebetween0,05 Withatestportionof0,5gandafinaldigestionvolumeo

    42、f20mlthelimitofquantificationforthefoodstuffwillbe calculatedbetween0,002mg/kgand0,2mg/kg.EN13806:2002(E) 7 9Precision 9.1General DetailsofaninterlaboratorytestontheprecisionofthemethodaresummarisedinannexA.Thevaluesderived fromthisinterlaboratorytestmaynotbeapplicabletoconcentrationrangesandmatrice

    43、sotherthanthosegiven. 9.2Repeatability Theabsolutedifferencebetweentwoindependentsingletestresults,obtainedwiththesamemethodonidentical testmaterialinthesamelaboratorybythesameoperatorusingthesameequipmentwithinashortintervaloftime, willinnotmorethan5%ofthecasesexceedthevaluesof rgiveninTable1. Table1Repeatability Sample x mg/kg r mg/kg BovineLiver,lyophilised 0,042 0,007 SaltWaterFish,homogenised 0,36 0


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