{ "@context" : { "@base" : "https://kodlistor.miljodatasamverkan.se/def/vocabulary/DATA_MATVARDE/ANALYS_MET/", "skos" : "http://www.w3.org/2004/02/skos/core#", "concepts" : "skos:Concept", "prefLabel" : "skos:prefLabel", "broader" : "skos:broader", "narrower" : "skos:narrower", "@language" : "sv", "VocabularyId" : "27", "ContinuityId" : "ed0019ed-a588-3b28-bc98-6a1fbaef6c55", "Identifier" : "ANALYS_MET", "Label" : "Analysmetod", "RegistrationStatus" : "Public draft", "IsWorkingCopy" : "false", "CheckedOutCopyId" : "0", "WorkingUser" : null, "DateModified" : "2026-04-22 18:39:42.0", "UserModified" : "staffan", "IsNumericConceptIdentifiers" : "false", "VocabularyType" : "Common", "FolderId" : "3", "FolderName" : "DATA_MATVARDE", "FolderLabel" : "Data Mätvärde", "IsNotationsEqualIdentifiers" : "false", "Definition" : null, "Version" : null }, "concepts" : [ { "@id" : "3500_Cr_B_Colorimetric_Method", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "3500_Cr_B_Colorimetric_Method", "@language" : "sv" } ], "VocabularyConceptId" : "362633", "VocabularyId" : "27", "Identifier" : "3500_Cr_B_Colorimetric_Method", "Label" : "3500_Cr_B_Colorimetric_Method", "Definition" : "3500-Cr B. Colorimetric Method. Standard Methods for the Examination of Water and Wastewater - This procedure measures only hexavalent chromium, (Cr6+). For total chromium determination, acid-digest the sample and follow with a suitable instrumental analysis technique. The hexavalent chromium is determined colorimetrically by reaction with diphenylcarbazide in acid solution. A red-violet colored complex of unknown composition is produced. The reaction is very sensitive", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "3500_Cr_B_Colorimetric_Method_2012", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "3500_Cr_B_Colorimetric_Method_2012", "@language" : "sv" } ], "VocabularyConceptId" : "362634", "VocabularyId" : "27", "Identifier" : "3500_Cr_B_Colorimetric_Method_2012", "Label" : "3500_Cr_B_Colorimetric_Method_2012", "Definition" : "3500-Cr B. Colorimetric Method-2012 Standard Methods for the Examination of Water and Wastewater - This procedure measures only hexavalent chromium, (Cr6+). For total chromium determination, acid-digest the sample and follow with a suitable instrumental analysis technique. The hexavalent chromium is determined colorimetrically by reaction with diphenylcarbazide in acid solution. A red-violet colored complex of unknown composition is produced. The reaction is very sensitive", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "4_NP_EKV", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "4_NP_EKV", "@language" : "sv" } ], "VocabularyConceptId" : "362635", "VocabularyId" : "27", "Identifier" : "4_NP_EKV", "Label" : "4_NP_EKV", "Definition" : "4-NP-ekvivalenter: Summan av 4-NP med (4-NP faktor 1) + (4-NP-E01 faktor 0,83) + (4-NP-E02 faktor 0,71)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "64_LFGB_L_00_00_115_2018_10_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "64_LFGB_L_00_00_115_2018_10_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362636", "VocabularyId" : "27", "Identifier" : "64_LFGB_L_00_00_115_2018_10_modifierad", "Label" : "64_LFGB_L_00_00_115_2018_10_modifierad", "Definition" : "§ 64 LFGB L 00.00-115:2018-10 (modifierad) (also: ASU L 00.00-115) Examination of foodstuffs - Determination of pesticide residues inplant-based foodstuffs - GC/MS and/or LC-MS/MS afteracetonitrile extraction/distribution and cleanup by dispersive SPE(QuEChERS) (Neufassung der Methode L 00.00-115 durch die Arbeitsgruppe \"Pestizide\" nach § 64 LFGB)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "64_LFGB_L_00_00_34_2010_09", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "64_LFGB_L_00_00_34_2010_09", "@language" : "sv" } ], "VocabularyConceptId" : "362637", "VocabularyId" : "27", "Identifier" : "64_LFGB_L_00_00_34_2010_09", "Label" : "64_LFGB_L_00_00_34_2010_09", "Definition" : "§ 64 LFGB L 00.00-34: 2010-09 Examination of food - Modular multimethod for determination of pesticide residues in foodstuff.(Modulare Multimethode zur Bestimmung vonPflanzenschutzmittelrückständen in Lebensmitteln(Erweiterte Neufassung der DFG-Methode S 19))", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "64_LFGB_L_06_00_3_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "64_LFGB_L_06_00_3_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362638", "VocabularyId" : "27", "Identifier" : "64_LFGB_L_06_00_3_modifierad", "Label" : "64_LFGB_L_06_00_3_modifierad", "Definition" : "§64 LFGB L 06.00-3 (modifierad) Determination of the mass of dry matter in meat and meat products - Gravimetric method - Reference method. (Untersuchung von Lebensmitteln - Bestimmung der Trockenmasse in Fleisch und Fleischerzeugnissen)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "64_LFGB_L_10_00_9", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "64_LFGB_L_10_00_9", "@language" : "sv" } ], "VocabularyConceptId" : "362639", "VocabularyId" : "27", "Identifier" : "64_LFGB_L_10_00_9", "Label" : "64_LFGB_L_10_00_9", "Definition" : "§64 LFGB L 10.00-9 Examination of food - Gas chromatographic determination of organotin compounds in fish and mussels (determination of mono, di, tri and tetrabutyltin, mono and dioctyltin, tricyclic hexyltin, mono, di and triphenyltin using GC-FPD in biota).Short method description:-\tDigestion with Tetramethylammonium hydroxide (TMAH)-\tDerivatisation with Natriumtetraethylborat (TEBOR)-\tExtraction with Hexane-\tClean up-\tMeasurement with GC-FPD (FPD = Flame Photometric Detector)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "64_LFGB_L_17_00_4", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "64_LFGB_L_17_00_4", "@language" : "sv" } ], "VocabularyConceptId" : "362640", "VocabularyId" : "27", "Identifier" : "64_LFGB_L_17_00_4", "Label" : "64_LFGB_L_17_00_4", "Definition" : "§64 LFGB L 17.00-4 Testing of foods - Determination of the total fat content in bread including biscuits of bread dough. (Untersuchung von Lebensmitteln - Bestimmung des Gesamtfettgehaltes in Brot einschließlich - Kleingebäck aus Brotteigen nach Säureaufschluss mittels Extraktion und Gravimetrie)Untersuchungsparameter: Fett, GesamtfettgehaltVerfahrensprinzipien: Säureaufschluss mittels Extraktion, Gravimetrie", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ACES_BFR", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ACES_BFR", "@language" : "sv" } ], "VocabularyConceptId" : "362641", "VocabularyId" : "27", "Identifier" : "ACES_BFR", "Label" : "ACES_BFR", "Definition" : "Bromanalys5 (ACES) - Brominated substances were analyzed on a GC using a 30 m x 0.25 mm, film thickness 0.25 µm TG5SilMS column connected to a mass spectrometer operating in electron capture negative ionization mode (NICI). Ammonia was used as the reaction gas and the mass fragments monitored were m/z 79 and 81 (Sellström et al., 1998)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ACES_CLC", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ACES_CLC", "@language" : "sv" } ], "VocabularyConceptId" : "362642", "VocabularyId" : "27", "Identifier" : "ACES_CLC", "Label" : "ACES_CLC", "Definition" : "GC/ECD-PCB/OCP3 (ACES) - Chlorinated substances , e.g. PCBs (PCB-28, -52, -101, -118, -153, -138+163, -180), HCB, pp'-DDT ((1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane) and its breakdown products pp'-DDE ((1,1'-(2,2-Dichloro-1,1-ethenediyl)bis(4-chlorobenzene)) and pp'-DDD ((1,1'-(2,2-Dichloro-1,1-ethanediyl)bis(4-chlorobenzene)) as well as the insecticide γ-HCH (hexachlorocyclohexane, Lindane) and its α- and β-isomers were analyzed on a gas chromatograph equipped with two EC-detectors. Two fused capillary columns were used in parallel: 60 m x 0.25 mm, film thickness 0.25 µm TG5MS respectively DB1701. Helium was used as carrier gas and Argon/Methane as make-up gas (Eriksson et al. 1997)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ACES_PFAS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ACES_PFAS", "@language" : "sv" } ], "VocabularyConceptId" : "362643", "VocabularyId" : "27", "Identifier" : "ACES_PFAS", "Label" : "ACES_PFAS", "Definition" : "UPLC-MS/MS (ACES) - Ultra performance liquid chromatography - tandem mass spectrometer - After extraction, the extract was transferred to an Eppendorf tube with ENVI-Carb and glacial acetic acid and vortex mixed. The extracts were centrifuged and transferred to a new Eppendorf tube. RSTD solution and NH4OAc in water was added. Extracts were warmed to room temperature, vortex mixed and centrifuged before transferred to auto sampler vial for UPLC-MS/MS analysis", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALDERSBEST_FISK", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALDERSBEST_FISK", "@language" : "sv" } ], "VocabularyConceptId" : "362644", "VocabularyId" : "27", "Identifier" : "ALDERSBEST_FISK", "Label" : "ALDERSBEST_FISK", "Definition" : "Åldersbestämning av fisk. Metod baserad på ”Metodhandbok för åldersbestämning av fisk”, Instutitionen för akvatiska resurser, SLU", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_B_DFHMS02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_B_DFHMS02", "@language" : "sv" } ], "VocabularyConceptId" : "362645", "VocabularyId" : "27", "Identifier" : "ALS_B_DFHMS02", "Label" : "ALS_B_DFHMS02", "Definition" : "ALS B-DFHMS02 - ALS analysmetod för bestämning av polykorerade dibensodioxiner och dibensofuraner (PCDD och PCDF) i biota. Analys enligt US EPA 1613B och SS EN 16190 med HR GC-MS. \"Determination of PCDD/Fs in enviro samples by isotope dilution method with the use of HRGC-HRMS. The procedure fulfils the conditions and requrements of the EPA 1613. Analysis includes spiking sample with 13C12 labeled extraction std., specific extraction method (toluen) by matrix ( including acid decomposition in the case of ash/slag samples), cleanup of a raw extract, fractionation and HRGC-HRMS measurement after addition of 13C12 labeled injection standard.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_B_GCMS_10_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_B_GCMS_10_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362646", "VocabularyId" : "27", "Identifier" : "ALS_B_GCMS_10_GBA", "Label" : "ALS_B_GCMS_10_GBA", "Definition" : "ALS B-GCMS-10/GBA - ALS analysmetod för bestämning av organofosfater och organofosfor-flamskyddsmedel i biota efter lösningsmedelsextraktion och mätning med GC-MS enligt PI-MA-M 03-079 2019-09. \"Samples are cold-extracted with hexane, acetone and methyl-tert-butyl ether (MTBE). The extract is measured with GC-MSD.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_B_PCBHMS02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_B_PCBHMS02", "@language" : "sv" } ], "VocabularyConceptId" : "362647", "VocabularyId" : "27", "Identifier" : "ALS_B_PCBHMS02", "Label" : "ALS_B_PCBHMS02", "Definition" : "ALS B-PCBHMS02 - ALS analysmetod för bestämning av dioxinlika PCB-kongener i biota. Analys enligt metod baserad på US EPA 1668A och SS-EN 16190. Mätning utförs med GC-HRMS. TEQ beräknas som summa toxiska ekvivalenter enligt WHO 2005 alternativt I-TEQ. \"Determination of indicator and dioxin-like PCBs in enviro samples by isotope dilution method with the use of HRGC-HRMS. SOP fullfills the conditions and requirements of the EPA 1668. Analysis includes spiking sample with 13C12 extraction std., specific extraction method by matrix, cleanup of a raw extract, fractionation and HRGC-HRMS measurement after addition of injection standard. Part of this procedure is moisture content determination in the case of solid samples.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_B_PCBHMS04", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_B_PCBHMS04", "@language" : "sv" } ], "VocabularyConceptId" : "362648", "VocabularyId" : "27", "Identifier" : "ALS_B_PCBHMS04", "Label" : "ALS_B_PCBHMS04", "Definition" : "ALS B-PCBHMS04 - ALS analysmetod för bestämning av PCB i biota. Analys enligt metod baserad på US EPA 1668A och SS-EN 16190. Mätning utförs med GC-HRMS. TEQ beräknas som summa toxiska ekvivalenter enligt WHO 2005 alternativt I-TEQ. \"Determination of indicator and dioxin-like PCBs in enviro samples by isotope dilution method with the use of HRGC-HRMS. SOP fullfills the conditions and requirements of the EPA 1668. Analysis includes spiking sample with 13C12 extraction std., specific extraction method by matrix, cleanup of a raw extract, fractionation and HRGC-HRMS measurement after addition of injection standard. Part of this procedure is moisture content determination in the case of solid samples.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_GLYFOSAT_AMPA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_GLYFOSAT_AMPA", "@language" : "sv" } ], "VocabularyConceptId" : "362649", "VocabularyId" : "27", "Identifier" : "ALS_GLYFOSAT_AMPA", "Label" : "ALS_GLYFOSAT_AMPA", "Definition" : "ALS: GLYFOSAT och AMPA - ALS analyspaket för bestämning av Glyfosat och Aminometylfosfonsyra (AMPA) i vatten. Analys utförs med LC-MS-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_M4", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_M4", "@language" : "sv" } ], "VocabularyConceptId" : "362650", "VocabularyId" : "27", "Identifier" : "ALS_M4", "Label" : "ALS_M4", "Definition" : "ALS-M4 - ALS analyspaket för bestämning av 10 metaller i biota med ICP-SFMS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OB_2", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OB_2", "@language" : "sv" } ], "VocabularyConceptId" : "362651", "VocabularyId" : "27", "Identifier" : "ALS_OB_2", "Label" : "ALS_OB_2", "Definition" : "ALS analyspaket OB-2a. Bestämning av PCB i biota med GC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OB_3A", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OB_3A", "@language" : "sv" } ], "VocabularyConceptId" : "362652", "VocabularyId" : "27", "Identifier" : "ALS_OB_3A", "Label" : "ALS_OB_3A", "Definition" : "ALS analyspaket OB-3a. Bestämning av klorerade pesticider i biota med GC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OB_4A", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OB_4A", "@language" : "sv" } ], "VocabularyConceptId" : "362653", "VocabularyId" : "27", "Identifier" : "ALS_OB_4A", "Label" : "ALS_OB_4A", "Definition" : "ALS-OB-4A - ALS analyspaket för bestämning av ftalater. Mätning utförs med GC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OJ_19A3Q", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OJ_19A3Q", "@language" : "sv" } ], "VocabularyConceptId" : "362654", "VocabularyId" : "27", "Identifier" : "ALS_OJ_19A3Q", "Label" : "ALS_OJ_19A3Q", "Definition" : "OJ-19a3Q Tennorganiska föreningar (3) (TBT låg rapp.gräns) i jord, slam och sediment. Bestämning av MBT, DBT, TBT. LOQ TBT=0,2 µg/kg TS. Analys enligt egen metod. Mätning med GC-ICP-SFMS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OJ_1_OXY_PAH", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OJ_1_OXY_PAH", "@language" : "sv" } ], "VocabularyConceptId" : "362655", "VocabularyId" : "27", "Identifier" : "ALS_OJ_1_OXY_PAH", "Label" : "ALS_OJ_1_OXY_PAH", "Definition" : "ALS OJ-1 Oxy-PAH - ALS analyspaket för bestämning av 9 Oxy-PAH (9-Fluorenon, 9,10-Antrakinon, 2-Metylantrakinon, 4H-Cyklopenta[def]fenantren-4-on, Benso[a]fluorenon, Bensantron, Bens[a]antracen-7,12-dion, 5,12-Naftacenkinon, 6H-Benzo[cd]pyren-6-on) i jord, slam och sediment. Mätningen utförs med GC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OJ_20C", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OJ_20C", "@language" : "sv" } ], "VocabularyConceptId" : "362656", "VocabularyId" : "27", "Identifier" : "ALS_OJ_20C", "Label" : "ALS_OJ_20C", "Definition" : "ALS Paket OJ-20C: Bestämning av oljeindex enligt metod CSN EN 14039 och TNRCC metod 1006. Mätning utförs med GC-FID.", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OV-21A_SPIMFAB", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OV-21A_SPIMFAB", "@language" : "sv" } ], "VocabularyConceptId" : "362657", "VocabularyId" : "27", "Identifier" : "ALS_OV-21A_SPIMFAB", "Label" : "ALS_OV-21A_SPIMFAB", "Definition" : "ALS Paket OV-21A: Bestämning av alifatfraktioner och aromatfraktioner. Bestämning av bensen, toluen, etylbensen och xylen (BTEX).Bestämning av polycykliska aromatiska kolväten, PAH (16 föreningar enligt EPA). Mätning utförs med GCMS enligt ALS interna instruktioner TKI74 och TKI41a som är baserade på SPIMFABs kvalitetsmanual.", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OV_2A", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OV_2A", "@language" : "sv" } ], "VocabularyConceptId" : "362658", "VocabularyId" : "27", "Identifier" : "ALS_OV_2A", "Label" : "ALS_OV_2A", "Definition" : "ALS Paket OV-2a: Bestämning av PCB7 i vatten enligt metod baserad på DIN 38407-3 och US EPA 8082. Mätning utförs med GC-ECD", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OV_3D", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OV_3D", "@language" : "sv" } ], "VocabularyConceptId" : "362659", "VocabularyId" : "27", "Identifier" : "ALS_OV_3D", "Label" : "ALS_OV_3D", "Definition" : "ALS analyspaket 3-d: Bestämning i vatten av Glyfosat och Aminometylfosfonsyra (AMPA). Analys utförs med LC-MS-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_OV_PFAS_SPE", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_OV_PFAS_SPE", "@language" : "sv" } ], "VocabularyConceptId" : "362660", "VocabularyId" : "27", "Identifier" : "ALS_OV_PFAS_SPE", "Label" : "ALS_OV_PFAS_SPE", "Definition" : "ALS OV-PFAS-SPE - ALS analysmetod för bestämning av PFAS i vatten enligt US EPA 533. ISTD (intern standard) tillsätts provet som därefter upparbetas med fast-fas-extraktion (SPE), PFAS extraheras med MeOH (metanol) för att sedan indunstas och därefter injiceras provet på instrumentet (LC-MS-MS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_PRIO", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_PRIO", "@language" : "sv" } ], "VocabularyConceptId" : "362661", "VocabularyId" : "27", "Identifier" : "ALS_PRIO", "Label" : "ALS_PRIO", "Definition" : "ALS interna metod för PRIO. Analys av PRIO-ämnen i ytvatten (Prioriterade ämnen enligt EU:s Water Frame Directive, WFD). Analys utförs med GC-MS, GC-MS-MS, GC-MS-MS-NCI eller LC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_PSO_1", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_PSO_1", "@language" : "sv" } ], "VocabularyConceptId" : "362662", "VocabularyId" : "27", "Identifier" : "ALS_PSO_1", "Label" : "ALS_PSO_1", "Definition" : "ALS analyspaket PSO-1 Bestämning i vatten av PAH (EPA-PAH, 15 st) med passiv provtagning och analys med HPLC-Fl/DAD och GC-MS. För bestämning av de tyngre PAHerna, används HPLC med fluorescens-detektor. För bestämning av de lättare PAHerna används GC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_PSO_11", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_PSO_11", "@language" : "sv" } ], "VocabularyConceptId" : "362663", "VocabularyId" : "27", "Identifier" : "ALS_PSO_11", "Label" : "ALS_PSO_11", "Definition" : "ALS analyspaket PSO-11 Bestämning i vatten av tributyltenn med passiv provtagning och analys med gaskromatograf med atomemissionsdetektor (GC_AED) enligt en modifiering av metoden: (EN ISO 17353 - Water quality — Determination of selected organotin compounds — Gas chromatographic method)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_PSO_12", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_PSO_12", "@language" : "sv" } ], "VocabularyConceptId" : "362664", "VocabularyId" : "27", "Identifier" : "ALS_PSO_12", "Label" : "ALS_PSO_12", "Definition" : "ALS analyspaket PSO-12 Bestämning i vatten av nonylfenol och oktylfenol med passiv provtagning och analys med GC-MS-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_PSO_2", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_PSO_2", "@language" : "sv" } ], "VocabularyConceptId" : "362665", "VocabularyId" : "27", "Identifier" : "ALS_PSO_2", "Label" : "ALS_PSO_2", "Definition" : "ALS analyspaket PSO-2 Bestämning i vatten av PCB 7 med passiv provtagning och analys med GC-ECD enligt en modifiering av metoden: (US EPA 1668 Determination of the toxic polychlorinated biphenyls (PCBs) in water, soil, sediment, sludge, tissue, and other sample matrices by isotope dilution and internal standard high-resolution gas chromatography/high-resolution mass spectrometry, HRGC/HRMS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_PSO_3", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_PSO_3", "@language" : "sv" } ], "VocabularyConceptId" : "362666", "VocabularyId" : "27", "Identifier" : "ALS_PSO_3", "Label" : "ALS_PSO_3", "Definition" : "ALS analyspaket PSO-3 Bestämning i vatten av klorerade pesticider med passiv provtagning och analys med GC-MS/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_PSO_5", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_PSO_5", "@language" : "sv" } ], "VocabularyConceptId" : "362667", "VocabularyId" : "27", "Identifier" : "ALS_PSO_5", "Label" : "ALS_PSO_5", "Definition" : "ALS analyspaket PSO-5 Bestämning i vatten av bromerade flamskyddsmedel med passiv provtagning och analys med GC-MS/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_SFA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_SFA", "@language" : "sv" } ], "VocabularyConceptId" : "362668", "VocabularyId" : "27", "Identifier" : "ALS_SFA", "Label" : "ALS_SFA", "Definition" : "ALS interna metod för mätning av SFÄ. Analys av SFÄ, Särskilt Förorenande Ämnen i vatten enligt HaV (Havs och vattenmyndigheten). Analys utförs med GC-MS-MS, GC-MS-MS-NCI, LC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_AEOGMS01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_AEOGMS01", "@language" : "sv" } ], "VocabularyConceptId" : "362669", "VocabularyId" : "27", "Identifier" : "ALS_S_AEOGMS01", "Label" : "ALS_S_AEOGMS01", "Definition" : "ALS S-AEOGMS01 - ALS analysmetod för bestämning av alkylfenoler och alkylfenoletoxylater enligt metod baserad på European Standard BT WI CSS99040. Mätning utförs med GC-MS eller GC-MS/MS. \"Alkylphenols and alkylphenol ethoxylates are extracted from the sample by an acetone/n-hexane mixture. The extracts are derivatised with MSTFA (silanisation) and determined by the gas chromatography with mass detection. The method is based on document European Standard BT WI CSS99040. The mixture of isomers (nonylphenol and nonylphenol mono- and diethoxylates) are identified by the fingerprint method. The quantification of the method is based on external calibration with subsequent correction to yield of surrogate standard.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_CLPGMS01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_CLPGMS01", "@language" : "sv" } ], "VocabularyConceptId" : "362670", "VocabularyId" : "27", "Identifier" : "ALS_S_CLPGMS01", "Label" : "ALS_S_CLPGMS01", "Definition" : "ALS S-CLPGMS01 - ALS analysmetod för bestämning av klorfenoler i jord, slam och sediment enligt metod baserad på US EPA 8041, US EPA 3500 and DIN ISO 14154. Mätning utförs med GC-MS. \"The method is based on extraction (acetone + hexane, K2CO3) of analytes from the sample into an organic solvent and a subsequent extraction into alkaline solution. Analytes in the alkaline solution are derivated to acetates that are subsequently transferred into non-polar organic solvent (hexane). The extract is analysed by gas chromatography with mass detection in SIM or GC-ECD regime. The quantification is performed by the method of internal standard with follow-up correction to yield of extraction standards.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_DFHMS03A", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_DFHMS03A", "@language" : "sv" } ], "VocabularyConceptId" : "362671", "VocabularyId" : "27", "Identifier" : "ALS_S_DFHMS03A", "Label" : "ALS_S_DFHMS03A", "Definition" : "ALS S-DFHMS03A - ALS analysmetod för bestämning av polykorerade dibensodioxiner och dibensofuraner (PCDD och PCDF) i jord, slam och sediment. Analys enligt US EPA 1613B och SS EN 16190 med HR GC-MS. \"Determination of PCDD/Fs in solid samples by isotope dilution method with the use of HRGC-HRMS. The procedure fulfils the conditions and requrements of the EPA 1613. Analysis includes spiking sample with 13C12 labeled extraction std., specific extraction method (toluen) by matrix ( including acid decomposition in the case of ash/slag samples), cleanup of a raw extract, fractionation and HRGC-HRMS measurement after addition of 13C12 labeled injection standard.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_DFPCBHMS03A_CC", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_DFPCBHMS03A_CC", "@language" : "sv" } ], "VocabularyConceptId" : "362672", "VocabularyId" : "27", "Identifier" : "ALS_S_DFPCBHMS03A_CC", "Label" : "ALS_S_DFPCBHMS03A_CC", "Definition" : "ALS S-DFPCBHMS03A-CC - ALS analysmetod för beräkning av TEQ för dioxiner och furaner samt dioxinlika PCB (kongener) enligt US EPA 1668A och SS-EN 16190. Mätning utförs med GC-HRMS. TEQ beräknas som summa toxiska ekvivalenter enligt WHO 2005 alternativt I-TEQ", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_DRY_GRCI", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_DRY_GRCI", "@language" : "sv" } ], "VocabularyConceptId" : "362673", "VocabularyId" : "27", "Identifier" : "ALS_S_DRY_GRCI", "Label" : "ALS_S_DRY_GRCI", "Definition" : "ALS S-DRY-GRCI - ALS analysmetod för bestämning av torrsubstans (TS) i jord, slam och sediment enligt metod baserad på CSN ISO 11465, CSN EN 12880 och CSN EN 14346:2007. \"Determination of dry matter by gravimetry and determination of moisture by calculation from measured values. This method determines the mass fraction of dry matter, moisture and water content in solid samples. The sample is dried to a constant weight at 105°C and from the difference in weights before and after drying, we determine the mass fraction of dry matter.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_CNT_CFA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_CNT_CFA", "@language" : "sv" } ], "VocabularyConceptId" : "362674", "VocabularyId" : "27", "Identifier" : "ALS_S_CNT_CFA", "Label" : "ALS_S_CNT_CFA", "Definition" : "S-CNT-CFA - ALS analysmetod för bestämning av total cyanid i jord, slam och sediment med spektrofotometri enligt metod baserad på CSN 75 7415, CSN EN ISO 17380, CSN EN ISO 14403-2 och SM 4500 CN. \"Determination of total cyanide by spectrophotometry and determination of complex-forming cyanides by calculation from measure values.The determination of total cyanide in solid matrices according to CSN EN ISO 17380, using continuous flow analysis with spectrophotometric detection, after releasing hydrogen cyanide in an acidic environment and separating it from the matrix by distillation. Thiocyanates are not included in total cyanides as there is no conversion to cyanides by CFA analysis. The determination of total cyanides (complex and free) is based on several reactions. Complex bound cyanides are decomposed by UV radiation with a wavelength of 312 nm at pH 3.8. Borosilicate spirals with a UV-B lamp prevent the conversion of thiocyanates to cyanides (filtering wavelengths smaller than 290 nm). The released cyanides are separated by distillation at 125°C and subsequently react with a solution of chloramine-T to form chlorkyan, which reacts with pyridine-4-carboxylic acid and 1,3-dimethylbarbituric acid to form a blue color. The absorbance of the colored solution is measured at a wavelength of 600 nm. The whole process is carried out using continuous flow analysis, which ensures the same conditions for distillation and the subsequent spectrophotometric measurement end of the entire analytical sequence.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_CR6_IC", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_CR6_IC", "@language" : "sv" } ], "VocabularyConceptId" : "362675", "VocabularyId" : "27", "Identifier" : "ALS_S_CR6_IC", "Label" : "ALS_S_CR6_IC", "Definition" : "ALS S-CR6-IC - ALS analysmetod för bestämning av Cr6+ i jord, slam och sediment efter alkalisk lakning enligt CSN EN 15192 och EPA 3060A. Mäning utförs med jonkromatografi. \"Determination of hexavalent chromium by ion chromatography with spectrophotometric detection and trivalent chromium determination by calculation from measured values. Small amount of soil sample is leached by alkaline solution. Filtered leachate is cleaned from interferences on annex column IonPac AS7. The Cr(VI) is determined by spectrophotometry at 530 nm after post-column reaction with 1,5- diphenylcarbazide in acidic environment. In the post-column derivatisation, diphenylcarbazide reacts with Cr(VI), creating Cr(II) and diphenylcarbazone. The latter two compounds create a complex with characteristic purple colour.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_DR_PFCLMS02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_DR_PFCLMS02", "@language" : "sv" } ], "VocabularyConceptId" : "362676", "VocabularyId" : "27", "Identifier" : "ALS_S_DR_PFCLMS02", "Label" : "ALS_S_DR_PFCLMS02", "Definition" : "ALS S-DR-PFCLMS02 - ALS analysmetod för bestämning av perflorerade och bromerade ämnen i jord, slam och sediment enligt metod baserad på DIN 38414-14. Mätningen utförs med LC-MS/MS. \"Determination of perfluorinated and brominated compounds by liquid chromatography with MS/MS detection. Soil samples are homogenised before starting sample preparation. The analysed sample is pre-dried before its own extraction (method code S-PPHOM 40C). The PFCs are determined with use of ultra-effective liquid chromatography in connection with mass spectrometry and direct injection. The direct injection method means that concentration or clean-up steps are not included, only the marked extraction standard is added, pH is adjusted and mechanical particles are removed by centrifugation and filtration or dilution. 2 g of homogenised pre-dried sample are put into a 50 ml plastic bottle. Into the sample is added 100 µl of ISTD 20 ng/ml solution and the sample is allowed to stand for at least 10 minutes and 10 ml of ACN/MeOH (1:1, v/v), the bottle is closed and mixed and allowed to stand for 20 min. After this time, 10 ml of the ACN/MeOH mixture (1:1, v/v) is added, the bottle is closed, shaken and left to stand for at least 20 minutes. Next, the bottle is mixed on a tilting shaker for 10 min and centrifuged (11000 RPM, 20 °C, 5 min). 6 ml of the extract is taken from the bottle into a 15 ml plastic bottle with pre-weighed Envicarb (in the amount of 50 mg of Envicarb per 1 ml of extract; therefore, 0.3 g of Envicarb is used for 6 ml of extract), shaken and put on a multi-position vortex (2500 rpm., 2 minutes). Then the sample is centrifuged (10000 RPM, 20 °C, 5 min.) and 5 ml of the purified extract is collected in a plastic 15 ml bottle with a blue cap. This extract is concentrated to a volume of 1 ml with a gentle stream of N2 . 200 µl of the extract is taken from the test bottle into a 2 ml screw-top vial with 600 µl of 5 mM ammonium acetate, the vial is closed with a septa-less polyethylene cap and mixed.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_GCMSD_2_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_GCMSD_2_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362677", "VocabularyId" : "27", "Identifier" : "ALS_S_GCMSD_2_GBA", "Label" : "ALS_S_GCMSD_2_GBA", "Definition" : "ALS S-GCMSD-2/GBA - ALS analysmetod för bestämning av siloxaner enligt GBA:s interna metod. Mätningen utförs med GC-MS. \"1 g of OS (original wet sample) are extracted with methyl-tert-butyl ether (MTBE) by ultrasonic treatment/shaker for 60 min. The extract is then measured on a GC-MS.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_GCMS_15_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_GCMS_15_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362678", "VocabularyId" : "27", "Identifier" : "ALS_S_GCMS_15_GBA", "Label" : "ALS_S_GCMS_15_GBA", "Definition" : "ALS S-GCMS-15/GBA - ALS analysmetod för bestämning av utvalda klorfenoler i jord, slam och sediment med GC-MS enligt DIN ISO 14154: 2005-12. \"Samples are extracted with methanol using ultrasonic and shaking treatment. The extract is derivatised and measured with GC-MSD.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_GCMS_1_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_GCMS_1_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362679", "VocabularyId" : "27", "Identifier" : "ALS_S_GCMS_1_GBA", "Label" : "ALS_S_GCMS_1_GBA", "Definition" : "ALS S-GCMS-1/GBA - ALS analysmetod för bestämning av ftalater i jord, slam och sediment enligt DIN 19742: 2014-08. Mätning utförs med GC-MS. \"Samples are extracted with ethylacetate on a shaker. The extract is measured with GC-MSD.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_GCMS_5_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_GCMS_5_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362680", "VocabularyId" : "27", "Identifier" : "ALS_S_GCMS_5_GBA", "Label" : "ALS_S_GCMS_5_GBA", "Definition" : "ALS S-GCMS-5/GBA - ALS analysmetod för bestämning av polybromerade difenyletrar i jord, slam och sediment enligt DIN EN ISO 22032: 2009-07. Mätningarna utförs med GC-MS. (DIN_EN_ISO_22032). \"Samples are extracted with toluene using soxhlet or ultrasonic treatment. The extract is cleaned, concentrated and measured with GC-MSD.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_GCMS_9_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_GCMS_9_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362681", "VocabularyId" : "27", "Identifier" : "ALS_S_GCMS_9_GBA", "Label" : "ALS_S_GCMS_9_GBA", "Definition" : "ALS S-GCMS-9/GBA - ALS analysmetod för bestämning av organofosfater och organofosfor-flamskyddsmedel i jord, slam och sediment efter lösningsmedelsextraktion och mätning med GC-MS enligt PI-MA-M 03-079 2019-09. \"Samples are extracted with acetone using ultrasonic and shaking treatment. The extract is measured with GC-MSD.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_GC_36", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_GC_36", "@language" : "sv" } ], "VocabularyConceptId" : "362682", "VocabularyId" : "27", "Identifier" : "ALS_S_GC_36", "Label" : "ALS_S_GC_36", "Definition" : "ALS S-GC-36 - ALS analysmetod för bestämning av metylkvicksilver i jord, slam och sediment med GC-ICP enligt SE-SOP-0026. \"Spikning: Invägning 0.5g-3g och tillsätt spiklösning: Lakning av metylkvicksilver: Tillsätt kopparsulftat lösning och sedan kaliumbromid-lösning, skakas försiktigt och låt reagera. Extraktion av metylkvicksliver: Tillsätt diklormetan, skakas 1h. Separation av lösningsmedlet: Återextraktion av metylkvicksilver. Filtrering av slamprovextrakt. Bestämning med GC-ICP.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_GC_46", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_GC_46", "@language" : "sv" } ], "VocabularyConceptId" : "362683", "VocabularyId" : "27", "Identifier" : "ALS_S_GC_46", "Label" : "ALS_S_GC_46", "Definition" : "ALS S-GC-46 - ALS analysmetod för bestämning av tennorganiska föreningar (OTC) i jord, slam och sediment. Analys med GC-ICP-MS enligt SE-SOP-0036 (SS-EN ISO 23161:2018). \"Icke torkade prover vägs in och lakas med en metanol/ättiksyra/H2O-blandning i ultraljudsbad. Sedan neutraliseras extraktionen med acetatbuffert samt natriumhydrixid. Efter det derivatiseras proverna i pentan m.h.a STEB (natriumtetraetylborat). Efter derivatiseringen tvättas pentanfasen och sedan sker analys på instrumentet.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_ICPAES_1_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_ICPAES_1_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362684", "VocabularyId" : "27", "Identifier" : "ALS_S_ICPAES_1_GBA", "Label" : "ALS_S_ICPAES_1_GBA", "Definition" : "ALS S-ICPAES-1/GBA - ALS analysmetod för bestämning av spårhalter i extrakt från jord enligt metod DIN ISO 22036:2009-06. Mätningen utförs med induktivt kopplat plasma - atomemissionspectrometry (ICP-AES)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_LCMS_GCMS_1_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_LCMS_GCMS_1_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362685", "VocabularyId" : "27", "Identifier" : "ALS_S_LCMS_GCMS_1_GBA", "Label" : "ALS_S_LCMS_GCMS_1_GBA", "Definition" : "ALS S-LCMS/GCMS-1/GBA. Paket OJ-27C. Bestämning av nitrotoluener/nitrobensener enligt metod Handbuch Altlasten Bd. 7 Teil 5. Bestämning av RDX, HMX, TNT, EGDN, DEGN, 1,3,5-trinitrobensen, nitroglycerin, nitropenta, hexyl samt tetryl enligt DIN ISO 11916-1:2014-11. Sample preparation according to DIN 19747:2009-07. Explosives according to DIN ISO 11916-1:2014-11 + DIN ISO 11916-2:2014-11. 10 g of sample and the internal standard were added and allowed to equilibrate. Extraction was then performed, followed by ultrasonic treatment for approximately 30 minutes, and subsequent shaking. The samples were then measured using LC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_LOI550", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_LOI550", "@language" : "sv" } ], "VocabularyConceptId" : "362686", "VocabularyId" : "27", "Identifier" : "ALS_S_LOI550", "Label" : "ALS_S_LOI550", "Definition" : "ALS S-LOI550 - ALS analysmetod för bestämning av glödgningsförlust (GF) och glödgningrest (GR) i jord, slam och sediment vid 550°C enligt SE-SOP-0067 (SS-EN 15935:2021). \"Determination of ash by gravimetry and calculation of loss on ignition from measure values. The dried samples are burned in the furnace at the specified temperature (550°C). From the difference in weight before and after burning, the loss on ignition is calculated, respectively the ignition residue.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_OCPECD01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_OCPECD01", "@language" : "sv" } ], "VocabularyConceptId" : "362687", "VocabularyId" : "27", "Identifier" : "ALS_S_OCPECD01", "Label" : "ALS_S_OCPECD01", "Definition" : "ALS S-OCPECD01 - ALS analysmetod för bestämning av klorerade pesticider och polyklorerade bifeyler (PCB) i jord, slam och sediment enligt metod baserad på US EPA 8081 och ISO 10382. Mätningen utförs med GC-ECD. \"Determination of organochlorine pesticides and other halogen compounds by gas chromatography method with ECD detection and calculation of organochlorine pesticides. Samples are extracted with acetone/hexane, cleaned by SPE (Florisil column) and mercury. After cleaning, the extract is concentrated. Individual OCPs are determinate by GC/ECD. The quantification is based on external calibration standard with correction of recovery of surrogate standard.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_OCPECD04", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_OCPECD04", "@language" : "sv" } ], "VocabularyConceptId" : "362688", "VocabularyId" : "27", "Identifier" : "ALS_S_OCPECD04", "Label" : "ALS_S_OCPECD04", "Definition" : "ALS S-OCPECD04 - ALS analysmetod för bestämning av klorerade pesticider och andra halogenerade ämnen i jord, slam och sediment enligt metod baserad på US EPA 8081 och ISO 10382. Mätningen utförs med GC-ECD. \"Determination of organochlorine pesticides and other halogen compounds by gas chromatography method with ECD detection and calculation of organochlorine pesticides. Samples are extracted with acetone/hexane, cleaned by SPE (Florisil column) and mercury. After cleaning, the extract is concentrated. Individual OCPs are determinate by GC/ECD. The quantification is based on external calibration standard with correction of recovery of surrogate standard.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_PCBHMS02A", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_PCBHMS02A", "@language" : "sv" } ], "VocabularyConceptId" : "362689", "VocabularyId" : "27", "Identifier" : "ALS_S_PCBHMS02A", "Label" : "ALS_S_PCBHMS02A", "Definition" : "ALS S-PCBHMS02A - ALS analysmetod för bestämning av dioxinlika PC-kongener i jord, slam och sediment. Analys enligt metod baserad på US EPA 1668A och SS-EN 16190. Mätning utförs med GC-HRMS. TEQ beräknas som summa toxiska ekvivalenter enligt WHO 2005 alternativt I-TEQ. \"Determination of indicator and dioxin-like PCBs in enviro samples by isotope dilution method with the use of HRGC-HRMS. SOP fullfills the conditions and requirements of the EPA 1668. Analysis includes spiking sample with 13C12 extraction std., specific extraction method by matrix, cleanup of a raw extract, fractionation and HRGC-HRMS measurement after addition of injection standard. Part of this procedure is moisture content determination in the case of solid samples.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_PESLMS02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_PESLMS02", "@language" : "sv" } ], "VocabularyConceptId" : "362690", "VocabularyId" : "27", "Identifier" : "ALS_S_PESLMS02", "Label" : "ALS_S_PESLMS02", "Definition" : "ALS S-PESLMS02 - ALS analysmetod för bestämning av pesticider i jord, slam och sediment enligt CSN EN 15637 och US EPA 1694. Mätning utförs med LC-MS/MS. \"Determination of pesticides, pesticide metabolites, drug residues and other pollutants by liquid chromatography method with MS/MS detection. Analytes are extracted from the sample using the QuEChERS method. The determination of pesticides is carried out by the method of liquid chromatography in conjunction with mass detection. The intensity of the decay of the mother ion into a daughter ion after the delivery of collision energy is monitored (multiple reaction monitoring, MRM). To confirm the result, two MRM transitions No. SANTE/11813/2017 are monitored for each analyte), a positive result is considered one when the ratio between the transitions corresponds to the ratio of the transitions in the standard. Quantification is performed using an external standard. The results are corrected for the yield of internal standards (external or internal calibration) and/or for the yield of the fortified blank.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_PESLMSA1", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_PESLMSA1", "@language" : "sv" } ], "VocabularyConceptId" : "362691", "VocabularyId" : "27", "Identifier" : "ALS_S_PESLMSA1", "Label" : "ALS_S_PESLMSA1", "Definition" : "S-PESLMSA1 - ALS analysmetod för bestämning av fenoxisyror och andra herbicider enligt metod baserad på CSN EN 15637 och US EPA 1694. Mätningenutförs med LC-MS/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_PFCLMS02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_PFCLMS02", "@language" : "sv" } ], "VocabularyConceptId" : "362692", "VocabularyId" : "27", "Identifier" : "ALS_S_PFCLMS02", "Label" : "ALS_S_PFCLMS02", "Definition" : "ALS S-PFCLMS02 - ALS analyspaket för bestämning av perfluorerade ämnen enligt metod baserad på DIN 38414-14. Provet homogeniseras innan upparbetning och analyseras med LC-MS/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_PHOTOMET_2_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_PHOTOMET_2_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362693", "VocabularyId" : "27", "Identifier" : "ALS_S_PHOTOMET_2_GBA", "Label" : "ALS_S_PHOTOMET_2_GBA", "Definition" : "ALS S-PHOTOMET-2/GBA - ALS analysmetod för bestämning av ammoniumkväve enligt DIN EN 12457-4: 2003-01. Analys av fast prov sker normalt i lakvatten enligt EN 12457-4:2003-01. Mätning utförs med flödesanalys (CFA och FIA) och spektrometrisk detektering", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_PTHGMS01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_PTHGMS01", "@language" : "sv" } ], "VocabularyConceptId" : "362694", "VocabularyId" : "27", "Identifier" : "ALS_S_PTHGMS01", "Label" : "ALS_S_PTHGMS01", "Definition" : "ALS S-PTHGMS01. Bestämning av ftalater enligt metod baserad på EPA 8061A och CPSC-CH-C1001-09.3. \"40 ml extraction solvent, dichlormethane is added to 5 g of sample. The extraction is done in ultrasonic bath for 20 minutes. Extract is transfered to a vial (after sedimentation), and 5 ml of n-hexane is added. This solution is concentrated down to 1 ml in two steps and then transfered to an analysis vial that is put into instrument autosampler (GC-MS)\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SFMS_16", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SFMS_16", "@language" : "sv" } ], "VocabularyConceptId" : "362695", "VocabularyId" : "27", "Identifier" : "ALS_S_SFMS_16", "Label" : "ALS_S_SFMS_16", "Definition" : "ALS S-SFMS-16 - ALS analyspaket för bestämning av metaller i fasta matriser enligt SS-EN ISO 17294-2:2016 och US EPA 200.8 (1994). Uppslutning av prov sker enligt ALS-metod S-PA 16-HB och analys utförs med ICP-SFMS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SFMS_49", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SFMS_49", "@language" : "sv" } ], "VocabularyConceptId" : "362696", "VocabularyId" : "27", "Identifier" : "ALS_S_SFMS_49", "Label" : "ALS_S_SFMS_49", "Definition" : "ALS S-SFMS-49 - ALS analyspaket för bestämning av metaller i fasta matriser enligt SS-EN ISO 17294-2:2016 och US EPA 200.8 (1994). Uppslutning av prov sker enligt ALS-metod S-PS49-FU och analys utförs med ICP-SFMS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SFMS_59", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SFMS_59", "@language" : "sv" } ], "VocabularyConceptId" : "362697", "VocabularyId" : "27", "Identifier" : "ALS_S_SFMS_59", "Label" : "ALS_S_SFMS_59", "Definition" : "ALS S-SFMS-59 - ALS analyspaket för bestämning av metaller i jord, slam, sediment och byggnadsmaterial enligt SS-EN ISO 17294-2:2016 och US EPA 200.8 (1994). Uppslutning av prov sker enligt ALS-metod S-PM59-HB och analys utförs med ICP-SFMS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SPIGMS04", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SPIGMS04", "@language" : "sv" } ], "VocabularyConceptId" : "362698", "VocabularyId" : "27", "Identifier" : "ALS_S_SPIGMS04", "Label" : "ALS_S_SPIGMS04", "Definition" : "S-SPIGMS04 - ALS analysmetod för bestämning av organiska föreningar i i jord, slam och sediment. Analys av organiska föroreningar-alifater >C5-C16 med GC-MS metod enligt SPIMFAB:s kvalitetsmanual", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_TOC1_IR", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_TOC1_IR", "@language" : "sv" } ], "VocabularyConceptId" : "362699", "VocabularyId" : "27", "Identifier" : "ALS_S_TOC1_IR", "Label" : "ALS_S_TOC1_IR", "Definition" : "ALS S-TOC1-IR - ALS analysmetod för bestämning av TOC i jord, slam och sediment enligt direkt metod; CSN ISO 10694, CSN EN 13137:2002, CSN EN 15936. \"Determination of total carbon (TC), total organic carbon (TOC) by the combustion method with IR detection and calculation of total inorganic carbon (TIC), carbonates and organic matter from measured values. Determination of TOC in solid samples after thermal decomposition with IR detection. The determination is performed on an analyzer Elementar soli TOC cube (M-1143). Analytical sample is weighed into porcelain cups and HCl (1: 1) is added to remove TIC (total inorganic carbon). The cup is dried in an oven at 70 °C. Then, the TOC is determined by IR detector.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SMLGMS01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SMLGMS01", "@language" : "sv" } ], "VocabularyConceptId" : "362700", "VocabularyId" : "27", "Identifier" : "ALS_S_SMLGMS01", "Label" : "ALS_S_SMLGMS01", "Definition" : "ALS S-SMLGMS01 CZ_SOP_D06_03_181 (US EPA 429, US EPA 1668, US EPA 3550) - ALS analysmetod för bestämning av semivolatila organiska ämnen i jord, slam och sediment med isotoputspädning och gaskromatografi med masspektrometri. Summor beräknas från uppmätta värden. Metoden har modifierats inom omfattningen för den flexibla ackrediteringen angiven i Annex to the Certificate of Accreditation No . 468/2020 utfärdad 27 juli 2020. Parametrar som inte ingår i bilagan till ackrediteringscertifikatet i parameter översikten under index 27 har lagts till. \"Determination of semi-volatile organic compounds by gas chromatography method with MS and calculation of semi-volatile organic compounds sums from measured values. The principle of the method is the microwave extraction of analytes from a sample of freeze-dried sea or river sediment into an organic solvent. The portion of the organic extract is concentrated and directly dosed into the gas chromatograph, where the analytes are separated on the chromatographic column and their detection is performed by a mass detector in the MRM (Multiple Reaction Monitoring) mode. Quantification is performed using the internal (extraction) standard method. The internal standard extraction method is classified according to EPA 8000C as a hybrid between the internal standard method and the isotopic dilution method. (http://www.epa.gov/osw/hazard/testmethods/pdfs/8000c_v3.pdf). An extraction (internal) standard is added into the freeze-dried philized sediment sample before extraction, which is otherwise commonly used as an internal standard added into extracts prior to injection into the gas chromatograph. These are either deuterated analogues of the target analytes, or substances very similar to the target analytes that do not occur in freeze dried sediment samples. These internal standards are also added in the same amount to the calibration solutions, and a calibration curve is constructed as a function of the ratio of the concentrations of the target analyte and the internal standard (x-axis) to the ratio of the responses of the target analyte and the internal standard (y-axis). The amount of analyte in the sample is calculated using the evaluation software MassHunter.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SMLGMS02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SMLGMS02", "@language" : "sv" } ], "VocabularyConceptId" : "362701", "VocabularyId" : "27", "Identifier" : "ALS_S_SMLGMS02", "Label" : "ALS_S_SMLGMS02", "Definition" : "S-SMLGMS02 - ALS analysmetod för bestämning och beräkning av semivolatila organiska ämnen i i jord, slam och sediment. Analys av PAH-16 och PCB-7 med isotoputspädning enligt US EPA 429, US EPA 1668, US EPA 3550. Mätning utförs med GC-MS. \"The principle of the method is the microwave extraction of analytes from a sample of freeze-dried sea or river sediment into an organic solvent (acetone+hexane, the final extract is in hexane). The portion of the organic extract is concentrated and directly dosed into the gas chromatograph, where the analytes are separated on the chromatographic column and their detection is performed by a mass detector in the MRM (Multiple Reaction Monitoring) mode. Quantification is performed using the internal (extraction) standard method. The internal standard extraction method is classified according to EPA 8000C as a hybrid between the internal standard method and the isotopic dilution method (http://www.epa.gov/osw/hazard/testmethods/pdfs/8000c_v3.pdf). An extraction (internal) standard is added into the freeze-dried philized sediment sample before extraction, which is otherwise commonly used as an internal standard added into extracts prior to injection into the gas chromatograph. These are either deuterated analogues of the target analytes, or substances very similar to the target analytes that do not occur in freeze dried sediment samples. These internal standards are also added in the same amount to the calibration solutions, and a calibration curve is constructed as a function of the ratio of the concentrations of the target analyte and the internal standard (x-axis) to the ratio of the responses of the target analyte and the internal standard (y-axis). The amount of analyte in the sample is calculated using the evaluation software MassHunter.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SMVGMS05", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SMVGMS05", "@language" : "sv" } ], "VocabularyConceptId" : "362702", "VocabularyId" : "27", "Identifier" : "ALS_S_SMVGMS05", "Label" : "ALS_S_SMVGMS05", "Definition" : "ALS S-SMVGMS05 Bestämning av semivolatila organiska föreningar med gaskromatografi med MS eller MS/MS samt beräkning av semivolatila föreningar och summor enligt US EPA 8270D, US EPA 8082A, CSN EN 15527, ISO 18287, ISO 10382, CSN EN 15308 och provberedning enligt US EPA 3546. \"Determination of semi volatile organic compounds by gas chromatography method with MS and calculation of semi volatile organic compounds sums from measured values. The determination of the content of extractable semi-volatile organic substances in waters (leaches) and solid samples by the method of gas chromatography with MS detection. The determination of semi-volatile substances is based on the US EPA 8082A method. The principle of the method is the extraction of semi-volatile organic substances from soil and water samples (leachates) into the appropriate solvent. After purification and concentration, the extract is dosed into a gas chromatograph, where analytes are separated on a chromatographic column. Their identification and detection is carried out by a mass detector. Quantification is performed using the external standard method followed by correction for the yield of the internal standard or is performed using the internal standard extraction method.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_TOC_CC", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_TOC_CC", "@language" : "sv" } ], "VocabularyConceptId" : "362703", "VocabularyId" : "27", "Identifier" : "ALS_S_TOC_CC", "Label" : "ALS_S_TOC_CC", "Definition" : "ALS S-TOC-CC - ALS analysmetod för bestämning av TOC beräknad från glödgningsförlust och baserad på “Van Bemmelen” faktorn. Glödgningsförlust bestämd enligt SS-EN15935:2021 utg2", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_TOC_GBA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_TOC_GBA", "@language" : "sv" } ], "VocabularyConceptId" : "362704", "VocabularyId" : "27", "Identifier" : "ALS_S_TOC_GBA", "Label" : "ALS_S_TOC_GBA", "Definition" : "ALS S-TOC/GBA - ALS analysmetod för bestämning av totalt organiskt kol (TOC) med torrförbränning enligt DIN EN 15936:2012-11", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_TPHFID01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_TPHFID01", "@language" : "sv" } ], "VocabularyConceptId" : "362705", "VocabularyId" : "27", "Identifier" : "ALS_S_TPHFID01", "Label" : "ALS_S_TPHFID01", "Definition" : "ALS S-TPHFID01 - ALS analysmetod för bestämning av oljeindex i jord, slam och sediment enligt metod CSN EN 14039, CSN EN ISO 16703, CSN P CEN ISO/TS 16558-2, US EPA 8015, US EPA 3550 och TNRCC metod 1006. Mätning utförs med GC-FID. \" Determination of extractable compounds in the range of hydrocarbons C10 - C40, their fractions calculated from the measured values by gas chromatography method with FID detection. A sample is extracted with acetone/hexane. The extract is decanted through sodium sulfate and cleaned up through silicagel because of elimination of polar compounds. After cleaning, the extract is concentrated or diluted. The quantification is based on external calibration standard.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_BISPHENOL_A_GEO91", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_BISPHENOL_A_GEO91", "@language" : "sv" } ], "VocabularyConceptId" : "362706", "VocabularyId" : "27", "Identifier" : "ALS_UK_BISPHENOL_A_GEO91", "Label" : "ALS_UK_BISPHENOL_A_GEO91", "Definition" : "ALS UK-geo91 Analysis of Bisphenol A in Surface Water, Groundwater and Saline Water. The method is a direct aqueous injection (DAI) procedure. Samples are analysed by highperformance liquid chromatography using a triple quadrupole mass spectrometer detector. Samples are injected on to a HPLC analytical column and analytes are separated from matrix interference. Analytes are identified and quantified with mass spectrometric detection in SRM mode. Quantitation is by an internal standard procedure. ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_EM_ORG_CONT_GEO83", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_EM_ORG_CONT_GEO83", "@language" : "sv" } ], "VocabularyConceptId" : "362707", "VocabularyId" : "27", "Identifier" : "ALS_UK_EM_ORG_CONT_GEO83", "Label" : "ALS_UK_EM_ORG_CONT_GEO83", "Definition" : "ALS UK-geo83 Analysis of Emerging Organic Contaminants for the EU water framework directive - Saline, Ground and Surface Waters. The compounds of interest are extracted from an aqueous matrix via Agilent’s online SPE system, equipped with a Hypersil Gold aQ pre-concentration column. The compounds are then flushed from the pre-concentration column via a gradient run and are separated on an Agilent Eclipse Plus C18 RRHD 3.0x55mm, 1.8um analytical column, before being ionised by Agilent’s Jetstream Electrospray technology, and analysed using MRM transitions on an Agilent 6470 LCMSMS. ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SPIGMS03", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SPIGMS03", "@language" : "sv" } ], "VocabularyConceptId" : "362708", "VocabularyId" : "27", "Identifier" : "ALS_S_SPIGMS03", "Label" : "ALS_S_SPIGMS03", "Definition" : "S-SPIGMS03 - ALS analysmetod för bestämning i jord, slam och sediment av: 1) Alifatfraktioner och aromatfraktioner. 2) Polycykliska aromatiska kolväten, PAH (16 föreningar enligt EPA). 4) Summa metylpyrener/metylfluorantener och summa metylkrysener/metylbens(a)antracener. GC-MS metod enligt SPIMFAB:s kvalitetsmanual. \"After addition of extraction standard, the sample is extracted with a pentane-methanol mixture with the final extract in pentane. After shaking with acidified water, the organic phase is isolated and analyzed by capillary gas chromatography with mass detection, when spectra are recorded in SIM or SIM/SCAN mode. Quantification is performed by the external standard method followed by corrections to the recovery of the extraction standard.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_SPIHSP01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_SPIHSP01", "@language" : "sv" } ], "VocabularyConceptId" : "362709", "VocabularyId" : "27", "Identifier" : "ALS_S_SPIHSP01", "Label" : "ALS_S_SPIHSP01", "Definition" : "ALS S-SPIHSP01 - ALS analysmetod för bestämning av volatila alifatiska och aromatiska kolväten i i jord, slam och sediment. Analys utförs med Headspace-GC-MS metod enligt SPIMFABs kvalitetsmanual. \"The weight of the sample is extracted with methanol in a closed vial after the adding of the surrogate standard and internal standards. An aliquot portion of the methanol extract is dosed into a HS vial, in which a defined volume of reagent water (15 ml) is presented and the vial is closed with a lid. The vial is incubated at a defined temperature and time. Vapors of volatile organic compounds are injected into a chromatographic column after the liquid-vapor interphase balance has been established, where they are separated. The separated compounds are identified by mass detector after recording spectra in SIM mode in the range of 35-200 amu. Quantification is performed by comparing the responses of identified substances in the sample and external standards followed by corrections to the response of internal standards.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_VOCGMS01", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_VOCGMS01", "@language" : "sv" } ], "VocabularyConceptId" : "362710", "VocabularyId" : "27", "Identifier" : "ALS_S_VOCGMS01", "Label" : "ALS_S_VOCGMS01", "Definition" : "S-VOCGMS01 - ALS analysmetod för bestämning av volatila organiska föreningar i i jord, slam och sediment: 1) BTEX. 2) Halogenerade volatila organiska föreningar. 2) Ickehalogenerade volatila organiska föreningar. Analysen utförs enligt metod baserad på US EPA 8260, US EPA 5021A, US EPA 5021, US EPA 8015, CSN EN ISO 22155, CSN EN 15009, CSN EN ISO 16558-1 och MADEP 2004, utgåva 1.1. Mätningen utförs med GC-FID och GC-MS. \"Solid sample is extracted into methanol in a closed vial. An aliquote part of the methanol extract is added to a headspace vial with a pre-defined amount of reagent water. The vial is incubated for the defined time and temperature. After establishing the liquid-gas equilibrium, the vapours of volatile organic compounds are injected to chromatographic column where they are separated. Separated compounds are identified in mass spectrometer and quantified in detector, based on the response magnitude of the amount of substance.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_S_VOCGMS04", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_S_VOCGMS04", "@language" : "sv" } ], "VocabularyConceptId" : "362711", "VocabularyId" : "27", "Identifier" : "ALS_S_VOCGMS04", "Label" : "ALS_S_VOCGMS04", "Definition" : "S-VOCGMS04 - ALS analysmetod för bestämning av flyktiga organiska föreningar i i jord, slam och sediment: Analys av: 1) Naftalen. 2) +Halogenerade volatila organiska föreningar. 3) Ickehalogenerade volatila organiska föreningar. Metod baserad på US EPA 8260, US EPA 5021A, US EPA 5021, US EPA 8015, CSN EN ISO 22155, CSN EN ISO 15009, CSN EN ISO 16558-1, MADEP 2004, rev. 1.1. Mätningen utförs med GC/MS och GC/FID. \"Solid sample is extracted into methanol in a closed vial. An aliquote part of the methanol extract is added to a headspace vial with a pre-defined amount of reagent water. The vial is incubated for the defined time and temperature. After establishing the liquid-gas equilibrium, the vapours of volatile organic compounds are injected to chromatographic column where they are separated. Separated compounds are identified in mass spectrometer and quantified in detector, based on the response magnitude of the amount of substance.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_HORMONES", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_HORMONES", "@language" : "sv" } ], "VocabularyConceptId" : "362712", "VocabularyId" : "27", "Identifier" : "ALS_UK_HORMONES", "Label" : "ALS_UK_HORMONES", "Definition" : "ALS UK Hormones: Determination of hormones in water. The compounds of interst are extracted from filtered aqueous matrix by solid phase extraction (SPE) and the extracts are further cleaned up by means of of another SPE procedure utilising a cartridge with a molecular imprinted polymer (MIP) stationary phase that has a class selective affinity for steroidal oestrogens. The isolated determinands are then derivatised with pentafluorobenzoyl chloride (PFBCI) and MSTFA and analysed by GC-MS-MS with negative chemical ionisation (NCI) using methane as the reagent gas. Quantification is based upon an internal standardisation procedure. ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_OCTYL_NONYLPHENOLS_GEO84", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_OCTYL_NONYLPHENOLS_GEO84", "@language" : "sv" } ], "VocabularyConceptId" : "362713", "VocabularyId" : "27", "Identifier" : "ALS_UK_OCTYL_NONYLPHENOLS_GEO84", "Label" : "ALS_UK_OCTYL_NONYLPHENOLS_GEO84", "Definition" : "ALS UK-geo84 Analysis of Octyl and Nonylphenols and their ethoxylates in Ground, Saline and Surface Waters. An automated extraction procedure is used to simultaneously extract the target compounds from aqueous matrix into hexane and derivatise them with Pentafluorobenzoyl Chloride to form the electron capturing Pentafluorobenzoyl derivatives. The extract is then analysed by GC-MSMS with negative chemical ionisation (NCI) using methane as the reagent gas. Quantification is based upon an internal standardisation procedure. ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_ORGANO_Cl_P_N_GEO47", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_ORGANO_Cl_P_N_GEO47", "@language" : "sv" } ], "VocabularyConceptId" : "362714", "VocabularyId" : "27", "Identifier" : "ALS_UK_ORGANO_Cl_P_N_GEO47", "Label" : "ALS_UK_ORGANO_Cl_P_N_GEO47", "Definition" : "ALS UK-geo47 Determination of a wide range of organochlorine, organophosphorous and organonitrogen compounds in Ground waters, Surface waters, Treated Sewage effluents, Trade effluents and Landfill leachates. A wide range of organic compounds are isolated from aqueous matrix using a two stage extraction technique. The compounds are determined by Electron impact GC-MSMS in selected reaction monitoring (SRM) mode using argon as a collision gas. ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_PAH_EPA16_GEO81", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_PAH_EPA16_GEO81", "@language" : "sv" } ], "VocabularyConceptId" : "362715", "VocabularyId" : "27", "Identifier" : "ALS_UK_PAH_EPA16_GEO81", "Label" : "ALS_UK_PAH_EPA16_GEO81", "Definition" : "ALS UK-geo81 Determination of PAH compounds (EPA16) in environmental waters - Surface Water, Land Leachate, Groundwater, Untreated Sewage, Treated Sewage and Trade Effluent. An automated dispersive liquid/liquid microextraction procedure (DLLME) is used to extract the PAH compounds from aqueous matrix. The dispersive solvent is a 1 % solution of toluene in isopropanol and the extraction solvent is a mixture of dichloromethane and n-pentane (80:20). The extract is then quantified by gas chromatography with mass spectrometric detection (GCMS). ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_PEST_NONPOLAR_ORG_GEO78", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_PEST_NONPOLAR_ORG_GEO78", "@language" : "sv" } ], "VocabularyConceptId" : "362716", "VocabularyId" : "27", "Identifier" : "ALS_UK_PEST_NONPOLAR_ORG_GEO78", "Label" : "ALS_UK_PEST_NONPOLAR_ORG_GEO78", "Definition" : "ALS UK-geo78 Analysis of Trace level Pesticides and selected non-polar organic compounds in Surface, Ground and Saline waters, Final effluents (TBT only). Approximately 400mls of sample is treated with sodium tetraethylborate (STEB) to ethylate TBT cation and is then extracted with 20mls of iso-hexane. The extract is analysed by GC-MSMS with electron impact (EI) ionisation. ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_LCMS_MS_2_HUM", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_LCMS_MS_2_HUM", "@language" : "sv" } ], "VocabularyConceptId" : "362717", "VocabularyId" : "27", "Identifier" : "ALS_W_LCMS_MS_2_HUM", "Label" : "ALS_W_LCMS_MS_2_HUM", "Definition" : "ALS W-LCMS-MS-2/HUM - ALS analysmetod för bestämning i vatten av ultrakorta perfluorerade ämnen, PFAS (5) i vatten. MeOH (metanol) och ISTD (intern standard) tillsätts provet som därefter injiceras direkt på instrumentet. Analys sker med LC-MS/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_PFAS_PEST_PHTAL_GEO82", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_PFAS_PEST_PHTAL_GEO82", "@language" : "sv" } ], "VocabularyConceptId" : "362718", "VocabularyId" : "27", "Identifier" : "ALS_UK_PFAS_PEST_PHTAL_GEO82", "Label" : "ALS_UK_PFAS_PEST_PHTAL_GEO82", "Definition" : "ALS UK-geo82 Analysis of Chloridazon, Bentazone, Metribuzin, Atrazine, Isoproturon, Diuron, Dichlorprop-p, Mecoprop,Pentachlorophenol, PFOS (Heptadecafluorooctanesulfonic acid), PFOA (Perfluoroctanoic acid) and DEHP (Diethylhexyl phthalate) in Surface, Ground and Saline waters. The compounds of interest are extracted from an aqueous matrix via online SPE, utilising Thermo Scientific’s EQuan LC system, equipped with a Hypersil Gold aQ pre-concentration column. The compounds are then backflushed from the pre-concentration column via a gradient run and are quantified by high resolution, accurate mass (HRAM) liquid chromatography mass spectrometry (LC-MS). ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_UK_VOC_GEO76", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_UK_VOC_GEO76", "@language" : "sv" } ], "VocabularyConceptId" : "362719", "VocabularyId" : "27", "Identifier" : "ALS_UK_VOC_GEO76", "Label" : "ALS_UK_VOC_GEO76", "Definition" : "ALS UK-geo76 Analysis of Volatile organic compounds (VOCs) by headspace in Ground waters, surface waters, landfill leachates and sewage and trade effluents. A 10 ml aliquot of water sample, preserved to pH<2 with HCl, is placed in a septum vial together with 1 ml of a sodium chloride based matrix modifying solution and allowed to equilibrate with its headspace vapour at 90°C. A sample of the vapour is injected using an automatic headspace sampler into a capillary column gas chromatograph (GC), the volatile organic compounds are separated and then identified and quantified using a mass spectrometer (MSD) simultaneously operating in selected ion monitoring (SIM) and full scan modes. ALS Environmental, Torrington Avenue, Coventry, CV4 9GU, United Kingdom", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_PESLMS04.", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_PESLMS04.", "@language" : "sv" } ], "VocabularyConceptId" : "362720", "VocabularyId" : "27", "Identifier" : "ALS_W_PESLMS04.", "Label" : "ALS_W_PESLMS04.", "Definition" : "ALS W-PESLMS04 - ALS analysmetod för bestämning i vatten av fenoxisyror och andra herbicider. Analys utförs enligt CZ SOP D06 03 182.A (DIN 38407-35, CEN/TS 15968). Mätningen utförs med LC-MS/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_PESLMS07", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_PESLMS07", "@language" : "sv" } ], "VocabularyConceptId" : "362721", "VocabularyId" : "27", "Identifier" : "ALS_W_PESLMS07", "Label" : "ALS_W_PESLMS07", "Definition" : "ALS W-PESLMS07 - ALS analysmetod för bestämning i vatten av pesticider, pesticidmetaboliter, läkemedelsrester och andra föroreningar. Analys utförs enligt CZ SOP D06 03 183.A (US EPA 535, US EPA 1694) genom vätskekromatografi med MS/MS-detektion och beräkning av pesticider, pesticidmetaboliter, läkemedelsrester och andra föroreningar summerade från uppmätta värden. Metoden har ändrats inom en flexibelt omfattande ackreditering, se ackrediteringsbevis nr 610/2017 daterad 16 oktober 2017. Det hänvisar till parametrarna: 2-amino-4-metoxi-6-metyl-1, 3,5-triazin, 3,5,6-triklorpyridin-2-ol, dimetaklor-CGA 369873, dimetenamid-ESA, dimetenamid-OA, flufenacet, flufenacet-ESA, flufenacet-OA, flutriafol, jodosulfuron-metyl, isoxaflutol, isoxaflutoldiketonitril, petoxamid-ESA, propazin-2-hydroxy, metolachlor-CGA 368208, metolachlor-NOA 413173, trietazin", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_RN222LSC", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_RN222LSC", "@language" : "sv" } ], "VocabularyConceptId" : "362722", "VocabularyId" : "27", "Identifier" : "ALS_W_RN222LSC", "Label" : "ALS_W_RN222LSC", "Definition" : "ALS W-RN222LSC - ALS analysmetod för bestämning av radon 222 enligt CSN 75 7625 (nukleär instrumenteringsräknare som utnyttjar flytande scintillatorer)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_SFMS_5ALK", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_SFMS_5ALK", "@language" : "sv" } ], "VocabularyConceptId" : "362723", "VocabularyId" : "27", "Identifier" : "ALS_W_SFMS_5ALK", "Label" : "ALS_W_SFMS_5ALK", "Definition" : "ALS W-SFMS-5ALK - ALS analysmetod för bestämning av halogener i sötvatten med ICP-SFMS enligt SS-EN ISO 17294-2:2023 och US EPA 200.8:1994", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_SFMS_5A_In", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_SFMS_5A_In", "@language" : "sv" } ], "VocabularyConceptId" : "362724", "VocabularyId" : "27", "Identifier" : "ALS_W_SFMS_5A_In", "Label" : "ALS_W_SFMS_5A_In", "Definition" : "ALS W-SFMS-5A-In - ALS analysmetod för analys av Indium (In) i sötvatten med ICP-SFMS enligt SS-EN ISO 17294-2:2023 och US EPA Method 200.8:1994. Provet är surgjort med 5 ml HNO3 (suprapur) per 100 ml före analys", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_SFMS_SO2_WFD", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_SFMS_SO2_WFD", "@language" : "sv" } ], "VocabularyConceptId" : "362725", "VocabularyId" : "27", "Identifier" : "ALS_W_SFMS_SO2_WFD", "Label" : "ALS_W_SFMS_SO2_WFD", "Definition" : "ALS W-SFMS-SO2-WFD - ALS analysmetod för analys av grundämnen i grundvatten (WFD grundvattendirektiv 2021) med ICP-SFMS enligt SS-EN ISO 17294-2:2023 och US EPA Method 200.8:1994", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ALS_W_SMVGMS02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ALS_W_SMVGMS02", "@language" : "sv" } ], "VocabularyConceptId" : "362726", "VocabularyId" : "27", "Identifier" : "ALS_W_SMVGMS02", "Label" : "ALS_W_SMVGMS02", "Definition" : "ALS W-SMVGMS02 - ALS analysmetod för bestämning i vatten av klorerade organiska insekticider, polyklorerade bifenyler och klorbensener. Analys utförs enligt SS-EN 6468, US EPA 8270D, US EPA 8082A och US EPA 8000. Mätning utförs med GC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ANALYTICA_BF", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ANALYTICA_BF", "@language" : "sv" } ], "VocabularyConceptId" : "362727", "VocabularyId" : "27", "Identifier" : "ANALYTICA_BF", "Label" : "ANALYTICA_BF", "Definition" : "ANALYTICA-BF. Bestämning av bisfenol med gaskromatografi-masspektrometri (GC-MSD), med Selected Ion Monitoring (SIM mode), där en CPSIL 8 CB MS-kolonn eller CPSIL 5 CB MS-kolonn användes. Slutligen utfördes en kvantifiering med extern standard", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "AOAC_2008_06", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "AOAC_2008_06", "@language" : "sv" } ], "VocabularyConceptId" : "362728", "VocabularyId" : "27", "Identifier" : "AOAC_2008_06", "Label" : "AOAC_2008_06", "Definition" : "AOAC Official Method 2008.06, AOAC INTERNATIONAL. Determination of moisture and fat in meats [Applicable for the determination of moisture and fat in meat and meat products (fresh, finished products and emulsions of beef, pork,and poultry).]. Microwave and Nuclear Magnetic Resonance Analysis", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "AR_EcoScreen", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "AR_EcoScreen", "@language" : "sv" } ], "VocabularyConceptId" : "362729", "VocabularyId" : "27", "Identifier" : "AR_EcoScreen", "Label" : "AR_EcoScreen", "Definition" : "AR-EcoScreen: Effektbaserad analys av AR (androgenreceptor)-aktivitet och anti-AR-aktivitet med luciferas gen-expression i celler från cellinjen AR-EcoScreen med ovarie-ursprung från kinesisk dvärghamster (Cricetulus griseus). Används i biotest för bestämning av AR-aktivitet och anti-AR-aktivitet.Cellinjen är stabilt transfekterad med den humana AR-receptorn samt en luciferas-reportergen. Mätbart ljus emitteras i respons till AR-aktivitet och anti-AR-aktivitet och detekteras av spektrofotometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "AZUR_ENV_1998", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "AZUR_ENV_1998", "@language" : "sv" } ], "VocabularyConceptId" : "362730", "VocabularyId" : "27", "Identifier" : "AZUR_ENV_1998", "Label" : "AZUR_ENV_1998", "Definition" : "Azur environmental-1998. The Microtox® acute basic, DIN, ISO and wet test procedures. Azur Environmental, Carlsbad, CA, USA, 1998", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "AhR_DR_EcoScreen", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "AhR_DR_EcoScreen", "@language" : "sv" } ], "VocabularyConceptId" : "362731", "VocabularyId" : "27", "Identifier" : "AhR_DR_EcoScreen", "Label" : "AhR_DR_EcoScreen", "Definition" : "AhR-DR-EcoScreen: Effektbaserat test av AhR (arylhydrokarbonreceptor/även kallad dioxinreceptor)-aktivitet med luciferas gen-expression i celler från cellinjen DR-EcoScreen från muslever-hepatom. Används i biotest för bestämning av polyklorerade dibenso-p-dioxiner (PCDD), polyklorerade dibensofuraner (PCDF) och dioxin-lika polyklorerade bifenyler (dl-PCB) i miljöprov och livsmedel. Cellinjen är stabilt transfekterad med mus-AhR(DR)-receporn samt en luciferas-reportergen. Mätbart ljus emitteras i respons till AhR-aktivitet och detekteras av spektrofotometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "Aquaref_MA_12", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "Aquaref_MA_12", "@language" : "sv" } ], "VocabularyConceptId" : "362732", "VocabularyId" : "27", "Identifier" : "Aquaref_MA_12", "Label" : "Aquaref_MA_12", "Definition" : "Aquaref MA 12 Bestämning av hormoner i vatten (Etinylöstradiol (CAS: 57-63-6) 17-beta-Östradiol (CAS: 50-28-2) Östron (CAS: 53-16-7) Östriol (CAS: 50-27-1). Upparbetning med fast-fas-extraktion (SPE) följt av analys med vätskekromatograf med tandem masspektrometer (LC-MS-MS). https://www.aquaref.fr/system/files/Aquaref_2013_D1b_Irstea_MA12-Hormone_estrogeniques_phase_dissoute_VF.pdf", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "BLV_L_00_00_12", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "BLV_L_00_00_12", "@language" : "sv" } ], "VocabularyConceptId" : "362733", "VocabularyId" : "27", "Identifier" : "BLV_L_00_00_12", "Label" : "BLV_L_00_00_12", "Definition" : "BLV L 00.00-12 Untersuchung von Lebensmitteln; Bestimmung von polychlorierten Biphenylen (PCB) in Lebensmitteln (§64 LFGB, Lebensmittel- und Futtermittelgesetzbuch)! 1993:08 Bundesamt für Verbraucherschutz und Lebensmittelsicherheit)(Determination of polychlorinated biphenyls (PCB) in food)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CEN_TS_16692-2015", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CEN_TS_16692-2015", "@language" : "sv" } ], "VocabularyConceptId" : "362734", "VocabularyId" : "27", "Identifier" : "CEN_TS_16692-2015", "Label" : "CEN_TS_16692-2015", "Definition" : "CEN/TS 16692:2015 Water quality - Determination of tributyltin (TBT) in whole water samples. Method using solid phase extraction (SPE) with SPE disks and gas chromatography with triple quadrupole mass spectrometry", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_46_5735", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_46_5735", "@language" : "sv" } ], "VocabularyConceptId" : "362735", "VocabularyId" : "27", "Identifier" : "CSN_46_5735", "Label" : "CSN_46_5735", "Definition" : "CSN 46 5735 Industrial composts", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_72_0103", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_72_0103", "@language" : "sv" } ], "VocabularyConceptId" : "362736", "VocabularyId" : "27", "Identifier" : "CSN_72_0103", "Label" : "CSN_72_0103", "Definition" : "CSN 72 0103 Basic procedure for the analysis of silicates - Determination of loss on ignition", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "AbfKlärV", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "AbfKlärV", "@language" : "sv" } ], "VocabularyConceptId" : "362737", "VocabularyId" : "27", "Identifier" : "AbfKlärV", "Label" : "AbfKlärV", "Definition" : "AbfKlärV Sewage sludge ordinance - the present Ordinance implements the Council Directive 86/278/EEC of 12 June 1986 on the protection of the environment and, in particular, of the soils where sewage sludge is, used in agriculture (Official Journal of the EC, no. L 181 p. 6). The said Ordinance has to be observed by anyone who 1. operates waste-water treatment plants and surrenders or intends to surrender sewage sludge for application on agriculturally or horticulturally used soils, 2. applies or intends to apply sewage sludge on agriculturally or horticulturally used soils. It consists of Sections as follows: Scope (1); Definition of terms (2); Conditions permitting application (3); Application bans and restrictions (4); Exemption regulations (5); Application quantity (6); Obligations to furnish verification (7); Application Schedule (8); Administrative offences (9); Entry into Force, abrogation (10). Two Annexes are enclosed. (Verordnung über die Verwertung von Klärschlamm, Klärschlammgemisch und Klärschlammkompost (Klärschlammverordnung - AbfKlärV)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "Anal_Chem_PFCAs_2005_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "Anal_Chem_PFCAs_2005_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362738", "VocabularyId" : "27", "Identifier" : "Anal_Chem_PFCAs_2005_modifierad", "Label" : "Anal_Chem_PFCAs_2005_modifierad", "Definition" : "Analytical Chemistry-PFCAs 2005 (modifierad). Matrix Effect-Free Analytical Methods for Determination of Perfluorinated Carboxylic Acids in Environmental Matrixes. Charles R. Powley, Stephen W. George, Timothy W. Ryan, and Robert C. Buck. Anal. Chem. 2005, 77, 19, 6353–6358. Publication Date:September 3, 2005.https://doi.org/10.1021/ac0508090. Perfluorocarboxylic acids (PFCAs) are persistent chemicals that have been found widely in the environment. Their accurate determination in environmental matrixes, particularly soil, sediment, and sludge, at low levels presents significant analytical challenges. The commercialization of electrospray interfaces for liquid chromatography−mass spectrometric analysis facilitated analysis of PFCAs at low levels, but issues with quantitative analysis due to matrix suppression or enhancement still persist. The methods described in this study utilize simple and rapid sample purification procedures to remove matrix components sufficiently so that errors due to coeluting matrix peaks are negligible and recoveries of PFCAs are consistently and reproducibly quantitative. Extracts from solid samples (soil and sediment) and liquid bacterial sludge are purified using dispersive solid-phase extraction. Recovery values generally are in the 70−120% range, with limits of quantitation of 1 ppb. The method utilizes an extraction solvent previously shown to release and recover aged residues of PFCAs. A confirmatory method using two precursor to product ions is also provided and demonstrated", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "BDS_AR_CALUX", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "BDS_AR_CALUX", "@language" : "sv" } ], "VocabularyConceptId" : "362739", "VocabularyId" : "27", "Identifier" : "BDS_AR_CALUX", "Label" : "BDS_AR_CALUX", "Definition" : "BDS-AR CALUX Analytical method from BioDetection Systems (BDS): Bioassay detection of androgen receptor activation (agonistic/antagonistic) of dihydrotestosterone (DHT). The samples were freeze dried, extracted with ASE (accelerated solvent extraction) with 100 % acetone, restituted in DMSO (dimethylsulfoxid) and subsequently measured in the CALUX bioassay. the AR CALUX bioassay comprises a human bone marrow cell line (U2OS), incorporating the firefly luciferase gene coupled to Androgen Responsive Elements (AREs) as a reporter gene. Following binding of androgen compounds to the intracellular androgen receptor, the ligand-receptor complex binds to and activates the ARE followed by expression of androgens and luciferace. By addition of substrate for luciferase, light is emitted which is measured in a luminometer. The amount of light produced is proportional to the amount of ligand-specific receptor binding, which is benchmarked against the reference compounds: dihydrotestosterone (agonistic) or flutamide (antagonistic). The amount of light of the samples is interpolated in the curve to obtain the reference equivalents. (Van der Burg, B., Van der Linden, S.C., Man, H.Y., Winter, R., Jonker, L., Van Vugt-Lussenburg, B., Brouwer, A. (2013) A panel of quantitative CALUX® reporter gene assays for reliable high throughput toxicity screening of chemicals and complex mixtures. In “High throughput screening methods in toxicity testing” (P. Steinberg, ed). John Wiley and Sons, Inc. New York. ISBN 9781118065631 pp. 519-532)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "BDS_DR_CALUX", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "BDS_DR_CALUX", "@language" : "sv" } ], "VocabularyConceptId" : "362740", "VocabularyId" : "27", "Identifier" : "BDS_DR_CALUX", "Label" : "BDS_DR_CALUX", "Definition" : "BDS-DR CALUX. Analytical method of BioDetection Systems (BDS): Bioassay detection of AhR (aryl-hydrocarbon receptor/dioxinreceptor)-activity coupled to presence of dioxins (PCDD/PCDF/dl-PCB). The samples were freeze dried, extracted with ASE (accelerated solvent extraction) with acetone/hexane (10%/90% v/v) followed by an additional acid silica column clean-up, restituted in DMSO (dimethylsulfoxid) and subsequently measured in the CALUX bioassay. The DR CALUX bioassay comprise a rat hepatoma cell line (H4IIE), incorporating the firefly luciferase gene coupled to Dioxin Responsive Elements (DREs) as a reporter gene. Following binding of dioxin compounds to the intracellular dioxin receptor, the ligand-receptor complex binds to and activates the DRE followed by expression of dioxins and luciferace. By addition of substrate for luciferase, light is emitted which is measured in a luminometer. The amount of light produced is proportional to the amount of ligand-specific receptor binding, which is benchmarked against the relevant reference compounds; for DR CALUX: 2,3,7,8-TCDD. The amount of light of the samples is interpolated in the curve to obtain the reference equivalents. (Van der Burg, B., Van der Linden, S.C., Man, H.Y., Winter, R., Jonker, L., Van Vugt-Lussenburg, B., Brouwer, A. (2013) A panel of quantitative CALUX® reporter gene assays for reliable high throughput toxicity screening of chemicals and complex mixtures. In “High throughput screening methods in toxicity testing” (P. Steinberg, ed). John Wiley and Sons, Inc. New York. ISBN 9781118065631 pp. 519-532)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_EN_12176", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_EN_12176", "@language" : "sv" } ], "VocabularyConceptId" : "362741", "VocabularyId" : "27", "Identifier" : "CSN_EN_12176", "Label" : "CSN_EN_12176", "Definition" : "CSN EN 12176 Characterization of sludge - Determination of pH-value", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_EN_12879", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_EN_12879", "@language" : "sv" } ], "VocabularyConceptId" : "362742", "VocabularyId" : "27", "Identifier" : "CSN_EN_12879", "Label" : "CSN_EN_12879", "Definition" : "CSN EN 12879 Characterisation of sludges - Determination of the loss on ignition of dry mass", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_EN_13137", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_EN_13137", "@language" : "sv" } ], "VocabularyConceptId" : "362743", "VocabularyId" : "27", "Identifier" : "CSN_EN_13137", "Label" : "CSN_EN_13137", "Definition" : "CSN EN 13137 Characterisation of waste - Determination of total organic carbon (TOC) in waste, sludges and sediments (2002)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_EN_13370", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_EN_13370", "@language" : "sv" } ], "VocabularyConceptId" : "362744", "VocabularyId" : "27", "Identifier" : "CSN_EN_13370", "Label" : "CSN_EN_13370", "Definition" : "CSN EN 13370", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_EN_1484", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_EN_1484", "@language" : "sv" } ], "VocabularyConceptId" : "362745", "VocabularyId" : "27", "Identifier" : "CSN_EN_1484", "Label" : "CSN_EN_1484", "Definition" : "CSN EN 1484", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "CSN_EN_15637", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "CSN_EN_15637", "@language" : "sv" } ], "VocabularyConceptId" : "362746", "VocabularyId" : "27", "Identifier" : "CSN_EN_15637", "Label" : "CSN_EN_15637", "Definition" : "CSN EN 15637 Foods of plant origin - 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The samples were freeze dried, extracted with ASE (accelerated solvent extraction) with 100% acetone, restituted in DMSO (dimethylsulfoxid) and subsequently measured in the CALUX bioassay. ER CALUX bioassay comprise a human breast cancer cell line (T47D), incorporating the firefly luciferase gene coupled to Estrogen Responsive Elements (EREs) as a reporter gene. Following binding of estrogen compounds to the intracellular estrogen alpha and beta receptors, the ligand-receptor complexes bind to and activate the ERE followed by expression of estrogens and luciferace. By addition of substrate for luciferase, light is emitted which is measured in a luminometer. The amount of light produced is proportional to the amount of ligand-specific receptor binding, which is benchmarked against the reference compound: 17β-estradiol. The amount of light of the samples is interpolated in the curve to obtain the reference equivalents. (Van der Burg, B., Van der Linden, S.C., Man, H.Y., Winter, R., Jonker, L., Van Vugt-Lussenburg, B., Brouwer, A. (2013) A panel of quantitative CALUX® reporter gene assays for reliable high throughput toxicity screening of chemicals and complex mixtures. In “High throughput screening methods in toxicity testing” (P. Steinberg, ed). John Wiley and Sons, Inc. New York. 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ERα CALUX bioassay comprises a human bone marrow cell line (U2OS), incorporating the firefly luciferase gene coupled to Estrogen Responsive Elements (EREs) as a reporter gene. Following binding of estrogen compounds to the intracellular estrogen alpha receptor, the ligand-receptor complex binds to and activates the ERE followed by expression of estrogens and luciferace. By addition of substrate for luciferase, light is emitted which is measured in a luminometer. The amount of light produced is proportional to the amount of ligand-specific receptor binding, which is benchmarked against the reference compounds: 17β-estradiol. The amount of light of the samples is interpolated in the curve to obtain the reference equivalents. (Van der Burg, B., Van der Linden, S.C., Man, H.Y., Winter, R., Jonker, L., Van Vugt-Lussenburg, B., Brouwer, A. (2013) A panel of quantitative CALUX® reporter gene assays for reliable high throughput toxicity screening of chemicals and complex mixtures. 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The PAH CALUX bioassay comprises a rat hepatoma cell line (H4IIE), incorporating the firefly luciferase gene coupled to Dioxin Responsive Elements (DREs) as a reporter gene. Following binding of PAH compounds to the intracellular dioxin receptor, the ligand-receptor complex binds to and activates the DRE followed by expression of PAH and luciferace. By addition of substrate for luciferase, light is emitted which is measured in a luminometer. The amount of light produced is proportional to the amount of ligand-specific receptor binding, which is benchmarked against the reference compound: Benzo[a]pyrene (B[a])P). The amount of light of the samples is interpolated in the curve to obtain the reference equivalents. (Van der Burg, B., Van der Linden, S.C., Man, H.Y., Winter, R., Jonker, L., Van Vugt-Lussenburg, B., Brouwer, A. (2013) A panel of quantitative CALUX® reporter gene assays for reliable high throughput toxicity screening of chemicals and complex mixtures. 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Mätbart ljus emitteras i respons till östrogen och östrogen-lika ämnen och detekteras av spektrofotometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ER_VM7Luc4E2", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ER_VM7Luc4E2", "@language" : "sv" } ], "VocabularyConceptId" : "362821", "VocabularyId" : "27", "Identifier" : "ER_VM7Luc4E2", "Label" : "ER_VM7Luc4E2", "Definition" : "ER-VM7Luc4E2: Effektbaserad analys av ER (östrogenreceptor)-aktivitet och anti-ER-aktivitet med luciferas gen-expression i celler från cellinjen VM7Luc4E2 med ursprung från humana bröstcancer-celler. Används i biotest för bestämning av human östrogenreceptor agonist- och antagonist-aktivitet av kemikalier. Testmetoden mäter i vilken utsträckning ett ämne inducerar eller inhiberar transkriptionell aktivitet via ER-medierade reaktioner.Cellinjen är stabilt transfekterad med östrogenreceptor samt en luciferas-reportergen. Mätbart ljus emitteras i respons till östrogen och östrogen-lika ämnen och detekteras av spektrofotometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "EU_2017_644", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "EU_2017_644", "@language" : "sv" } ], "VocabularyConceptId" : "362822", "VocabularyId" : "27", "Identifier" : "EU_2017_644", "Label" : "EU_2017_644", "Definition" : "EU-förordning 2017/644 - Om provtagnings- och analysmetoder för kontroll av halter av dioxiner, dioxinlika PCB och icke- dioxinlika PCB i vissa livsmedel och om upphävande av förordning (EU) nr 589/2014", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "E_DIN_ISO_13877", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "E_DIN_ISO_13877", "@language" : "sv" } ], "VocabularyConceptId" : "362823", "VocabularyId" : "27", "Identifier" : "E_DIN_ISO_13877", "Label" : "E_DIN_ISO_13877", "Definition" : "E DIN ISO 13877 Soil quality - Determination of polynuclear aromatic hydrocarbons — Method using high -performance liquid chromatography", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "FASTFAS_EXTR_Cu", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "FASTFAS_EXTR_Cu", "@language" : "sv" } ], "VocabularyConceptId" : "362824", "VocabularyId" : "27", "Identifier" : "FASTFAS_EXTR_Cu", "Label" : "FASTFAS_EXTR_Cu", "Definition" : "Fast fas-extraktion av koppar med \"multilayer SPE (SPE: solid phase extraction); for soil/sediment/sludge an additional activated copper treatment is applied\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "GBA_PI_MA_M_02_028_2019_09", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "GBA_PI_MA_M_02_028_2019_09", "@language" : "sv" } ], "VocabularyConceptId" : "362825", "VocabularyId" : "27", "Identifier" : "GBA_PI_MA_M_02_028_2019_09", "Label" : "GBA_PI_MA_M_02_028_2019_09", "Definition" : "GBA Gesellschaft für Bioanalytik mbH, In-house method PI-MA-M 02-028: 2019-09 - Determination of selected PFAS in water, solids and biota by LC-MS/MS after solid phase extraction", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "GBA_PI_MA_M_02_028_2023_06", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "GBA_PI_MA_M_02_028_2023_06", "@language" : "sv" } ], "VocabularyConceptId" : "362826", "VocabularyId" : "27", "Identifier" : "GBA_PI_MA_M_02_028_2023_06", "Label" : "GBA_PI_MA_M_02_028_2023_06", "Definition" : "GBA Gesellschaft für Bioanalytik mbH, In-house method PI-MA-M 02-028: 2023-06 - Determination of selected PFAS in water, solids and biota by LC-MS/MS after solid phase extraction", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "GBA_PI_MA_M_03_112_2017_02", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "GBA_PI_MA_M_03_112_2017_02", "@language" : "sv" } ], "VocabularyConceptId" : "362827", "VocabularyId" : "27", "Identifier" : "GBA_PI_MA_M_03_112_2017_02", "Label" : "GBA_PI_MA_M_03_112_2017_02", "Definition" : "GBA Gesellschaft für Bioanalytik mbH, analytic method PI-MA-M 03-112: 2017-02 - Analysis of estrogens, estrogen metabolites and sitosterol in water and soil samples", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "GRAVIMETRI", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "GRAVIMETRI", "@language" : "sv" } ], "VocabularyConceptId" : "362828", "VocabularyId" : "27", "Identifier" : "GRAVIMETRI", "Label" : "GRAVIMETRI", "Definition" : "Gravimetri. Gravimetrisk analys eller viktanalys avser inom kemi analytiska metoder för att bestämma halten av ett ämne i ett prov med hjälp av ytterst noggranna analysvågar", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "GR_GeneBLAzer", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "GR_GeneBLAzer", "@language" : "sv" } ], "VocabularyConceptId" : "362829", "VocabularyId" : "27", "Identifier" : "GR_GeneBLAzer", "Label" : "GR_GeneBLAzer", "Definition" : "GR-GeneBLAzer: Effektbaserad analys av GR (glukokortikoid-receptor)-aktivitet som ett mått på immun- och inflammations-respons i celler från cellinjen GeneBLAzer®UAS-bla HEK 293T med ursprung i humana embryoala njurceller. Cellinjen är stabilt transkriberad med human glukokortikoid-receptor (GR) och en beta-laktamas reportergen. När en agonist binder till receptorn bildas beta-laktamas vilken kan mätas som fluorescens", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "HC_EF_IMP_2016", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "HC_EF_IMP_2016", "@language" : "sv" } ], "VocabularyConceptId" : "362830", "VocabularyId" : "27", "Identifier" : "HC_EF_IMP_2016", "Label" : "HC_EF_IMP_2016", "Definition" : "HELCOM Guidelines for monitoring of biological effect - imposex and intersex (2016)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "HGDMA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "HGDMA", "@language" : "sv" } ], "VocabularyConceptId" : "362831", "VocabularyId" : "27", "Identifier" : "HGDMA", "Label" : "HGDMA", "Definition" : "HgDMA - Bestämning av kvicksilver. Direkt förbränning, amalgamering och analys med atomabsorptionsspektrometri (AAS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "HepG2_NFκB", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "HepG2_NFκB", "@language" : "sv" } ], "VocabularyConceptId" : "362832", "VocabularyId" : "27", "Identifier" : "HepG2_NFκB", "Label" : "HepG2_NFκB", "Definition" : "HepG2-NFκB: Effektbaserad analys av NFκβ (\"nuclear factor: kappa light chain enhancer of activated B cells\")-aktivitet som ett mått på immun- och inflammations-respons med luciferas gen-expression i celler från cellinjen HepG2-NFκβ i celler från humant hepatom. Cellinjen är stabilt transfekterad med NFκβ-responsivt element samt en luciferas-reportergen Mätbart ljus emitteras i respons till NFκβ-aktivitet och detekteras av spektrofotometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_10694", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_10694", "@language" : "sv" } ], "VocabularyConceptId" : "362833", "VocabularyId" : "27", "Identifier" : "ISO_10694", "Label" : "ISO_10694", "Definition" : "ISO 10694 Soil quality - Determination of organic and total carbon after dry combustion (elementary analysis)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_12010", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_12010", "@language" : "sv" } ], "VocabularyConceptId" : "362834", "VocabularyId" : "27", "Identifier" : "ISO_12010", "Label" : "ISO_12010", "Definition" : "ISO 12010", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_13878", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_13878", "@language" : "sv" } ], "VocabularyConceptId" : "362835", "VocabularyId" : "27", "Identifier" : "ISO_13878", "Label" : "ISO_13878", "Definition" : "ISO 13878 Soil quality - Determination of total nitrogen content by dry combustion (\"elemental analysis\")", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_15923_1_2013", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_15923_1_2013", "@language" : "sv" } ], "VocabularyConceptId" : "362836", "VocabularyId" : "27", "Identifier" : "ISO_15923_1_2013", "Label" : "ISO_15923_1_2013", "Definition" : "ISO 15923-1:2013 Water quality — Determination of selected parameters by discrete analysis systems — Part 1: Ammonium, nitrate, nitrite, chloride, orthophosphate, sulfate and silicate with photometric detection", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_15923_1_2013_C", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_15923_1_2013_C", "@language" : "sv" } ], "VocabularyConceptId" : "362837", "VocabularyId" : "27", "Identifier" : "ISO_15923_1_2013_C", "Label" : "ISO_15923_1_2013_C", "Definition" : "ISO 15923-1:2013 Water quality — Determination of selected parameters by discrete analysis systems — Part 1: Ammonium, nitrate, nitrite, chloride, orthophosphate, sulfate and silicate with photometric detection. Annex C: Determination of nitrate and nitrite by the hydrazine method", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_18857_2_2009", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_18857_2_2009", "@language" : "sv" } ], "VocabularyConceptId" : "362838", "VocabularyId" : "27", "Identifier" : "ISO_18857_2_2009", "Label" : "ISO_18857_2_2009", "Definition" : "ISO 18857-2:2009 Water quality — Determination of selected alkylphenols — Part 2: Gas chromatographic-mass spectrometric determination of alkylphenols, their ethoxylates and bisphenol A in non-filtered samples following solid-phase extraction and derivatisation", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_21458_2008", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_21458_2008", "@language" : "sv" } ], "VocabularyConceptId" : "362839", "VocabularyId" : "27", "Identifier" : "ISO_21458_2008", "Label" : "ISO_21458_2008", "Definition" : "ISO 21458:2008 Water quality — Determination of glyphosate and AMPA — Method using high performance liquid chromatography (HPLC) and fluorometric detection", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_21458_2008_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_21458_2008_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362840", "VocabularyId" : "27", "Identifier" : "ISO_21458_2008_modifierad", "Label" : "ISO_21458_2008_modifierad", "Definition" : "ISO 21458:2008 (modifierad) Water quality — Determination of glyphosate and AMPA — Method using high performance liquid chromatography (HPLC) and fluorometric detection", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_21675_2019", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_21675_2019", "@language" : "sv" } ], "VocabularyConceptId" : "362841", "VocabularyId" : "27", "Identifier" : "ISO_21675_2019", "Label" : "ISO_21675_2019", "Definition" : "ISO 21675:2019 Water quality — Determination of perfluoroalkyl and polyfluoroalkyl substances (PFAS) in water — Method using solid phase extraction and liquid chromatography-tandem mass spectrometry (LC-MS/MS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_28540_2011", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_28540_2011", "@language" : "sv" } ], "VocabularyConceptId" : "362842", "VocabularyId" : "27", "Identifier" : "ISO_28540_2011", "Label" : "ISO_28540_2011", "Definition" : "ISO 28540:2011 Water quality - Determination of 16 polycyclic aromatic hydrocarbons (PAH) in water - Method using gas chromatography with mass spectrometric detection (GC-MS) (ISO 28540:2011 specifies a method for the determination of at least 16 selected PAH (see Table 1) in drinking water and ground water in mass concentrations above 0,005 µg/l and surface water in mass concentrations above 0,01 µg/l (for each individual compound). 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It is possible that this method is applicable to other PAH, provided the method is validated for each case.)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_29441_2010", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_29441_2010", "@language" : "sv" } ], "VocabularyConceptId" : "362843", "VocabularyId" : "27", "Identifier" : "ISO_29441_2010", "Label" : "ISO_29441_2010", "Definition" : "Water quality - Determination of total nitrogen after UV digestion - Method using flow analysis (CFA and FIA) and spectrometric detection", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_7150_1_1984", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_7150_1_1984", "@language" : "sv" } ], "VocabularyConceptId" : "362844", "VocabularyId" : "27", "Identifier" : "ISO_7150_1_1984", "Label" : "ISO_7150_1_1984", "Definition" : "ISO 7150-1:1984 Water quality - Determination of ammonium - Part 1: Manual spectrometric method", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_TS_15923_2_2017", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_TS_15923_2_2017", "@language" : "sv" } ], "VocabularyConceptId" : "362845", "VocabularyId" : "27", "Identifier" : "ISO_TS_15923_2_2017", "Label" : "ISO_TS_15923_2_2017", "Definition" : "ISO/TS 15923-2:2017 Water quality - Determination of selected parameters by discrete analysis systems -- Part 2: Chromium(VI), fluoride, total alkalinity, total hardness, calcium, magnesium, iron, iron(II), manganese and aluminium with photometric detection", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ISO_TS_17182_2014", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ISO_TS_17182_2014", "@language" : "sv" } ], "VocabularyConceptId" : "362846", "VocabularyId" : "27", "Identifier" : "ISO_TS_17182_2014", "Label" : "ISO_TS_17182_2014", "Definition" : "ISO/TS 17182:2014 Soil quality - Determination of some selected phenols and chlorophenols -- Gas chromatographic method with mass spectrometric detection", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ITM_PFAS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ITM_PFAS", "@language" : "sv" } ], "VocabularyConceptId" : "362847", "VocabularyId" : "27", "Identifier" : "ITM_PFAS", "Label" : "ITM_PFAS", "Definition" : "ITM-PFAS Undersökningar av biota. Vätskekromatografimasspektrometri(LC/MS-MS). Kvantifieringen utfördes genom att matris liknande den som skaanalyseras tillsattes referenssubstans i olika mängd och sedan extraherades och upparbetades somproven. Responsen för proven jämfördes sedan med responsen för de spikade matriserna.", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_A10", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_A10", "@language" : "sv" } ], "VocabularyConceptId" : "362848", "VocabularyId" : "27", "Identifier" : "IVL_A10", "Label" : "IVL_A10", "Definition" : "IVL-metod A10 för bestämning av metylkvicksilver i  sediment/jord utförs med en analysmetod som bygger på ”EPA-1630”, primär separation genom destillation följt av etylering i vattenfas, gaskromatografisk separation och atomfluorescensspektrometri", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_A12", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_A12", "@language" : "sv" } ], "VocabularyConceptId" : "362849", "VocabularyId" : "27", "Identifier" : "IVL_A12", "Label" : "IVL_A12", "Definition" : "IVL-metod A12 för analys av kvicksilver i biota. Upparbetning och analys följer IVL:s metod A12: Bestämning av kvicksilver med AFS. Fasta prover uppsluts i en blandning av koncentrerad HNO3/H2SO4 med återloppskokning. För att säkerställa fullständig oxidation till Hg(II) behandlas provet dessutom med extra oxidationsmedel och späds sedan med SQ-vatten. Därefter reduceras kvicksilvret till Hg0 med reduktionsmedel och samlas upp på guldfälla genom purge and trap-metod med N2 som bärgas, följt av dubbel guld-amalgamering och detektering med Cold Vapour Atomic Fluorescence Spectroscopy (CV-AFS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_A19", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_A19", "@language" : "sv" } ], "VocabularyConceptId" : "362850", "VocabularyId" : "27", "Identifier" : "IVL_A19", "Label" : "IVL_A19", "Definition" : "IVL-metod A19 för analys av PCB7, PBDE, DDT och HCB i biota. Upparbetning och analys av samtliga ämnen följer IVL:s metod A19: Gaskromatografisk bestämning av PCB (verifierad mot SS-EN 16167:2018+AC:2019 och till EN ISO 6468:1996). 10 g provmaterial väges in och spikas med internstandard. Prover extraheras i 15 ml aceton i två omgångar och med pentan:eter (9:1) i två omgångar i ultraljudsbad (15 min/gång), vätske/vätske-extraheras med pentan:eter (9:1), upprenas med svavelsyrabehandling och fraktioneras genom en aluminiumoxidkolonn innan analys. Analysen utförs på en gaskromatograf (GC) där olika ämnen separeras på en kapillärkolonn innan de detekteras på en elektroninfångnings-detektor, ECD. Analyterna kvantifieras mot en kalibrerkurva och analysens riktighet kontrolleras med referenslösningar med känd halt. Utbyten korrigeras med hjälp av internstandarden", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_FLOT", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_FLOT", "@language" : "sv" } ], "VocabularyConceptId" : "362851", "VocabularyId" : "27", "Identifier" : "IVL_FLOT", "Label" : "IVL_FLOT", "Definition" : "IVL method IVL-FLOT - Determination of flotation chemicals used in the mining industry was carried out using a liquid chromatography-mass spectrometer (LC-MS/MS). Sample volume was extracted using solid-phase extraction (SPE) columns with a WAX phase (Cleanert PWAX, Phenomenex, WA1506), then eluted with 5/95 (v/v) ammonia (25%)/methanol, and analyzed using an Acquity UPLC BEH C18 column. Final analysis was performed on a Shimadzu LCMS-8050 system, including two gradient pumps (LC-40D x3), an autosampler (SIL-40C X3), and a column oven (CTO-40C). The flow rate was set to 0.3 mL/min, and the injection volume was 4 µL. The gradient program consisted of A: MQ-water with 0.12% ammonia (25%) and B: ACN", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_MESILOX", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_MESILOX", "@language" : "sv" } ], "VocabularyConceptId" : "362852", "VocabularyId" : "27", "Identifier" : "IVL_MESILOX", "Label" : "IVL_MESILOX", "Definition" : "IVL-MESILOX. Slamundersökningar - Bestämning av siloxaner med GC-MS. Proven analyseras med purge&trap, termal desorption och GC-MS-SIR ienlighet med IVL-rapport B1643 (http://www3.ivl.se/rapporter/pdf/B1643.pdf)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_PAH", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_PAH", "@language" : "sv" } ], "VocabularyConceptId" : "362853", "VocabularyId" : "27", "Identifier" : "IVL_PAH", "Label" : "IVL_PAH", "Definition" : "IVL-PAH - Determination of PAH components was carried out using a high performance liquid chromatograph (HPLC, type Agilent 1290, with a 3 μm C18-column (Pursuit PAH 100* 3 mm, Agilent). A linear gradient elution program was used, starting with acetonitrile/water 50:50 and ending with 100% acetonitrile (Rathburne HPLC-grade). A fluorescence detector (Agilent 1260) with a wavelength program optimised for each PAH was used for quantification. The peak heights were registered with a chromatographic system from Thermo (Chromeleon 7.0). The concentrations of 16 different PAH compounds were calculated by comparison to a certified standard, NIST, SRM 1647f (Priority Pollutant Polycyclic Aromatic Hydrocarbons in Acetonitrile)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_TENNORG", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_TENNORG", "@language" : "sv" } ], "VocabularyConceptId" : "362854", "VocabularyId" : "27", "Identifier" : "IVL_TENNORG", "Label" : "IVL_TENNORG", "Definition" : "IVL-Tennorganiska - A six point calibration curve was prepared by diluting Organotin mix 8 stock solution (LGC Promochem) to which fresh solutions of monophenyltin trichloride and diphenyltin dichloride in methanol had been added. After ethylation using sodium tetraethylborate water was added and the ethylates extracted with hexane. Instrumental analysis was carried out using a 7890A gas chromatograph connected to a 7010 triple quadrupole mass spectrometer (Agilent) used in electron ionization and multiple reaction monitoring (MRM) mode. For most compounds two MRMs were recorded, one as a quantifier and the other as a qualifier to increase specificity", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_YES", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_YES", "@language" : "sv" } ], "VocabularyConceptId" : "362855", "VocabularyId" : "27", "Identifier" : "IVL_YES", "Label" : "IVL_YES", "Definition" : "IVL-YES: Vattenundersökningar - Bestämning av östrogena effekter. Proven extraheras med fast fas-extraktion, elueras med aceton, överförs genom lösningsmedels-utbyte till dimetylsulfoxid och detekteras med fotometri i enlighet med IVL-rapport B 1483 (https://www.ivl.se/download/18.343dc99d14e8bb0f58b7414/1445515503373/B1483.pdf)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "Journ_of_Chrom-PEST_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "Journ_of_Chrom-PEST_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362856", "VocabularyId" : "27", "Identifier" : "Journ_of_Chrom-PEST_modifierad", "Label" : "Journ_of_Chrom-PEST_modifierad", "Definition" : "Journal of Chromatography A 1217 (2010) 2933–2939 (modifierad). Development of a simple extraction and clean-up procedure for determination of organochlorine pesticides in soil using gas chromatography–tandem mass spectrometry", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "IVL_PFAS_BIOTA", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "IVL_PFAS_BIOTA", "@language" : "sv" } ], "VocabularyConceptId" : "362857", "VocabularyId" : "27", "Identifier" : "IVL_PFAS_BIOTA", "Label" : "IVL_PFAS_BIOTA", "Definition" : "IVL-PFAS BIOTA. IVL-metod för bestämning av PFAS i biota. 1 g homogeniserat prov vägs in. En blandning av isotopinmärkta internstandarder som motsvarar de ämnen som skall analyseras tillsätts till varje prov, med en tillsatt mängd av 10 ng per ämne. Proverna ekvilibreras sedan vid rumstemperatur i 30 minuter före extraktion i ultraljudsbad med 2 × 5 ml metanol. Extrakten kombineras och koncentreras till 1 ml under kvävgas följt av ett uppreningssteg via tillsats av 25 mg aktivt kol (graphitized carbon black, GCB). Partiklarna avlägsnas genom centrifugering. Sedan tas 0,5 ml av provet och tillsätts till 0,5 ml lösning av ammoniumacetat i vatten. Ämnen som faller ut efter denna tillsats avlägsnas genom centrifugering innan proverna analyseras med vätskekromatografi med masspektrometrisk detektion", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "LECO_RC612_TOC", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "LECO_RC612_TOC", "@language" : "sv" } ], "VocabularyConceptId" : "362858", "VocabularyId" : "27", "Identifier" : "LECO_RC612_TOC", "Label" : "LECO_RC612_TOC", "Definition" : "LECO RC612 Temperature-dependent determination of Total Organic Carbon (TOC) in Soil, Rock, and Shale using LECO RC612 analysis. The temperature-dependent method requires no sample pretreatment and no additional sample preparation. With the assumption that organic species decompose to CO2 between 150 oC to 450 oC, and inorganic species below 1000 oC, heating to these specific temperatures in an oxidizing environment allows differentiation of the TOC from the Total Inorganic Carbon (TIC).", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "MACHNAGEL_1993_11", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "MACHNAGEL_1993_11", "@language" : "sv" } ], "VocabularyConceptId" : "362859", "VocabularyId" : "27", "Identifier" : "MACHNAGEL_1993_11", "Label" : "MACHNAGEL_1993_11", "Definition" : "Macherey-Nagel 1993-11 Bestämning av pentaklorfenol med GC_MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "MADEP_2004_rev_1_1", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "MADEP_2004_rev_1_1", "@language" : "sv" } ], "VocabularyConceptId" : "362860", "VocabularyId" : "27", "Identifier" : "MADEP_2004_rev_1_1", "Label" : "MADEP_2004_rev_1_1", "Definition" : "MADEP 2004, rev. 1.1 - Method for the determination of extractable petroleum hydrocarbons (eph)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "MoLab_LAKEM_MIKROFOR", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "MoLab_LAKEM_MIKROFOR", "@language" : "sv" } ], "VocabularyConceptId" : "362861", "VocabularyId" : "27", "Identifier" : "MoLab_LAKEM_MIKROFOR", "Label" : "MoLab_LAKEM_MIKROFOR", "Definition" : "MoLab (Laboratorium för organisk spåranalys vid Högskolan Kristianstad, Krinova Incubator & Science Park). Bestämning av läkemedel och mikroföreningar - Multimetod för analys av mikroföroreningar (såsom läkemedelsrester, bekämpningsmedel och PFAS) i vatten och slam. Provet, som lagrats i frys fram till analys, tinas. Vattenproverna surgörs och upparbetas med Solid Phase Extraktion (SPE). Slutanalys sker med kromatografi (tre metoder på tre kolonner; sur, basisk och neutral) i kombination med masspektrometri (UPLC-MS/MS). Varje analyserat ämne har optimerats till respektive kromatografisk metod med avseende på känslighet och separerbarhet. Metoden utförs enligt \"Whole water analysis\", d v s hela provet analyseras utan filtrering, vilket efterfrågas på EUs Watchlist. Metoden är inte ackrediterad, men validerad mot standardmetod 1694 (US EPA, 2007). Mikroföroreningar i slam extraheras med ultraljud och vidare provupparbetning sker med SPE. Slutanalys sker med UPLC-MS/MS enligt ovan beskrivna metod", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "NEN_5756", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "NEN_5756", "@language" : "sv" } ], "VocabularyConceptId" : "362862", "VocabularyId" : "27", "Identifier" : "NEN_5756", "Label" : "NEN_5756", "Definition" : "NEN 5756 Soil - Determination of organic and total carbon in soil after dry combustion (\"Element analysis\")", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "NMKL_160_1998_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "NMKL_160_1998_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362863", "VocabularyId" : "27", "Identifier" : "NMKL_160_1998_modifierad", "Label" : "NMKL_160_1998_modifierad", "Definition" : "NMKL 160-1998 (modifierad), (Nordic Committee on Food Analysis, NMKL) Fat. Determination in foods. The sample is boiled in dilute hydrochloric acid in order to, among other things, liberate bound fat and convert salts of fatty acids to free acids. After filtration and gentle drying, the residue is extracted with petroleum ether or hexane. The solvent is distilled off and the mass of the residue determined. This method describes a standardised procedure for the determination of the total fat content in foods after extraction. It is a general method applicable to most solid foods with the exception of pure milk products and food fats. The results of the method performance study gave acceptable results for sausage, gruel powder, cheese, biscuits, potato chips and ice cream. For fish, oats and banana/avocado, however, the results from the study were unacceptable. See also section 12. The extracted fat may be analysed for fatty acid composition. For other normal determinations made on fat more careful extraction methods must be used", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "NMKL_161_1998_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "NMKL_161_1998_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362864", "VocabularyId" : "27", "Identifier" : "NMKL_161_1998_modifierad", "Label" : "NMKL_161_1998_modifierad", "Definition" : "NMKL 161-1998 (modifierad), (Nordic Committee on Food Analysis, NMKL) Metals. Determination by atomic absorption spectrophotometry after wet digestion in a microwave oven. This method describes quantitative determination of the metals: lead, cadmium, zinc, copper and iron in various types of foods, with the exception of oils, fats and extremely fatty products. The method employs atomic absorption spectrophotometry (AAS) after microwave oven digestion under pressure. The method has been tested on dry materials only, but may under certain conditions be used for samples containing water. The sample is wet digested with nitric acid and hydrogen peroxide in a sealed container heated by microwaves. The sample solution is diluted with water and the concentrations of the metals are determined by flame or graphite furnace AAS. (Recommended by Codex as type III method)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "Nrf2_AREc32", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "Nrf2_AREc32", "@language" : "sv" } ], "VocabularyConceptId" : "362865", "VocabularyId" : "27", "Identifier" : "Nrf2_AREc32", "Label" : "Nrf2_AREc32", "Definition" : "Nrf2-AREc32: Effektbaserad analys av Nrf2 (\"transcription factor: nuclear factor erythroid-2-related factor 2\")-aktivitet som ett mått på oxidativ stress med luciferas gen-expression i celler från cellinjen AREc32 med ursprung från humana bröstcancer-celler. Biotest med cell-linjen AREc32 baseras på induktion av de Nrf2-ARE-medierade oxidativa stress-respons reaktionerna vilka är responsiva för många kemikalier som orsakar oxidativ stress, t.ex. ett stort antal pesticider och hud-irriterande ämnen. Cellinjen är stabilt transfekterad med \"antioxidant response element\" (ARE) samt en luciferas-reportergen. Mätbart ljus emitteras i respons till Nrf2-aktivitet och detekteras av spektrofotometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ORU_MTM_EOF_SLAM", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ORU_MTM_EOF_SLAM", "@language" : "sv" } ], "VocabularyConceptId" : "362866", "VocabularyId" : "27", "Identifier" : "ORU_MTM_EOF_SLAM", "Label" : "ORU_MTM_EOF_SLAM", "Definition" : "Analysmetod för Extraherbart Organiskt Fluor (EOF) i slam (Örebro universitet (ORU), Forskningscentrum Människa-Teknik-Miljö (MTM). 0,5 g torrsubstans (TS) extraheras med metanol och upprenas med ENVI-Carb. Analys utförs med förbränningsjonkromatografi (CIC)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ORU_MTM_PFAS_SLAM", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ORU_MTM_PFAS_SLAM", "@language" : "sv" } ], "VocabularyConceptId" : "362867", "VocabularyId" : "27", "Identifier" : "ORU_MTM_PFAS_SLAM", "Label" : "ORU_MTM_PFAS_SLAM", "Definition" : "Analysmetod för PFAS i slam (Örebro universitet (ORU), Forskningscentrum Människa-Teknik-Miljö (MTM). 0,5 g torrsubstans (TS) extraheras med metanol och upprenas med ENVI-Carb. Märkta standarder tillsätts före och efter extraktion. Analys utförs med UPLC-MS/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "ORU_MTM_PFAS_UtgVatt", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "ORU_MTM_PFAS_UtgVatt", "@language" : "sv" } ], "VocabularyConceptId" : "362868", "VocabularyId" : "27", "Identifier" : "ORU_MTM_PFAS_UtgVatt", "Label" : "ORU_MTM_PFAS_UtgVatt", "Definition" : "Analysmetod för PFAS i utgående vatten från reningsverk och avlopp (Örebro universitet (ORU), Forskningscentrum Människa-Teknik-Miljö (MTM). Utgående vatten (effluent) pH-justeras till 4 och filtreras genom 1 µm glasfiberfilter. 250 ml extraheras med mix-mode svag anjonbytare (WAX). Märkta standarder tillsätts före och efter extraktion och provet injiceras både på UPLC-MS/MS och SFC-MS/MS för analys", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "PFAS_VERREAULT_2007", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "PFAS_VERREAULT_2007", "@language" : "sv" } ], "VocabularyConceptId" : "362869", "VocabularyId" : "27", "Identifier" : "PFAS_VERREAULT_2007", "Label" : "PFAS_VERREAULT_2007", "Definition" : "Analys av PFAS enligt metoden i \"Verreault et al., Trends of Perfluorinated Alkyl Substances in Herring Gull Eggs from Two Coastal Colonies in Northern Norway:  1983−2003, Environmental Science & Technology, 2007, 41, 6671-6677\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "PI_MA_M_02_024_2019_09 ", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "PI_MA_M_02_024_2019_09 ", "@language" : "sv" } ], "VocabularyConceptId" : "362870", "VocabularyId" : "27", "Identifier" : "PI_MA_M_02_024_2019_09 ", "Label" : "PI_MA_M_02_024_2019_09 ", "Definition" : "PI-MA-M 02-024: 2019-09, GBA Gesellschaft für Bioanalytik mbH In-house method - Determination of selected active substances of plant protection products by LC-MS/MS in water and soil", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "PREN_17505_2020", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "PREN_17505_2020", "@language" : "sv" } ], "VocabularyConceptId" : "362871", "VocabularyId" : "27", "Identifier" : "PREN_17505_2020", "Label" : "PREN_17505_2020", "Definition" : "prEN 17505:2020 Soil and waste characterization - Temperature dependent differentiation of total carbon (TOC400, ROC, TIC900)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "PSA_MM_MERC", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "PSA_MM_MERC", "@language" : "sv" } ], "VocabularyConceptId" : "362872", "VocabularyId" : "27", "Identifier" : "PSA_MM_MERC", "Label" : "PSA_MM_MERC", "Definition" : "PSA Millennium Merlin mercury. Determination of mercury by utilising atomic fluorescence as a detection technique with a Millennium Merlin mercury analyser from P S Analytical. The Millennium Merlin is linear to 10ppm. Typical applications include environmental samples such as ground water, drinking water, food stuffs (e.g. milk, fish & tea), soils & sludges, biological samples (e.g. urine, blood and hair), industrial samples such as effluent, aluminium, zinc electrolytes, paper, incineration ash, sodium hypocholite, caustic soda, fly ash, sulfur, brine and petrochemical chemical samples including; naphthas, crude oil, condensates, formation waters and other petrochemcial products", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "Pb_TOT", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "Pb_TOT", "@language" : "sv" } ], "VocabularyConceptId" : "362873", "VocabularyId" : "27", "Identifier" : "Pb_TOT", "Label" : "Pb_TOT", "Definition" : "Pb was determined by monitoring 208Pb in high resolution using ICP-HRMS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "QUANT_BLACK_CARBON", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "QUANT_BLACK_CARBON", "@language" : "sv" } ], "VocabularyConceptId" : "362874", "VocabularyId" : "27", "Identifier" : "QUANT_BLACK_CARBON", "Label" : "QUANT_BLACK_CARBON", "Definition" : "Metod beskriven i \"Gustafsson et al., 2001. Evaluation of a protocol for the quantification of black carbon in sediments. Global Biogeochemical Cycles, 15, 881-890.\"", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "QuEChERS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "QuEChERS", "@language" : "sv" } ], "VocabularyConceptId" : "362875", "VocabularyId" : "27", "Identifier" : "QuEChERS", "Label" : "QuEChERS", "Definition" : "QuEChERS (\"quick, easy, cheap, effective, rugged, and safe\"). Solid-phase extraction method for detection of pesticide residues in food. The sample (fruits, vegetables, tobacco, etc.) is homogenized and centrifuged with a reagent and agitated for 1 minute. The reagents used depend on the type of sample to be analyzed. Following this, the sample is put through a dispersive solid phase extraction cleanup prior to analysis by gas-liquid chromatography or liquid-liquid chromatography. F. J. Schenck and J. E. Hobbs (July 2004). \"Evaluation of the Quick, Easy, Cheap, Effective, Rugged, and Safe (QuEChERS) Approach to Pesticide Residue Analysis\". Bulletin of Environmental Contamination and Toxicology. New York: Springer. 73 (1): 24–30. doi:10.1007/s00128-004-0388-y", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "RPS_ETHINYL_ESTRADIOL", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "RPS_ETHINYL_ESTRADIOL", "@language" : "sv" } ], "VocabularyConceptId" : "362876", "VocabularyId" : "27", "Identifier" : "RPS_ETHINYL_ESTRADIOL", "Label" : "RPS_ETHINYL_ESTRADIOL", "Definition" : "RPS Mountainheath Ltd analytical method of ethinyl estradiol in water. Solid Phase Extraction is followed by fraction collection and analysis on LC-MS/MS in multiple reaction monitoring mode (MRM)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SAKNAS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SAKNAS", "@language" : "sv" } ], "VocabularyConceptId" : "362877", "VocabularyId" : "27", "Identifier" : "SAKNAS", "Label" : "SAKNAS", "Definition" : "Saknas, information ej tillgänglig", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SCA90", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SCA90", "@language" : "sv" } ], "VocabularyConceptId" : "362878", "VocabularyId" : "27", "Identifier" : "SCA90", "Label" : "SCA90", "Definition" : "SCA90", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_4500_C_D_modifierad_MOLYBDAT_SI", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_4500_C_D_modifierad_MOLYBDAT_SI", "@language" : "sv" } ], "VocabularyConceptId" : "362879", "VocabularyId" : "27", "Identifier" : "SGS_4500_C_D_modifierad_MOLYBDAT_SI", "Label" : "SGS_4500_C_D_modifierad_MOLYBDAT_SI", "Definition" : "SGS Std.Met. 4500-C,D modifierad Vattenundersökningar - Bestämning av molybdatreaktivt kisel vilket analyserar mängden löst kisel. Uppslutning med ? och analys med ?", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_Aqua_Ref_MA_12", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_Aqua_Ref_MA_12", "@language" : "sv" } ], "VocabularyConceptId" : "362880", "VocabularyId" : "27", "Identifier" : "SGS_Aqua_Ref_MA_12", "Label" : "SGS_Aqua_Ref_MA_12", "Definition" : "SGS Aqua-Ref MA 12. Analyspaket SGS Analytics - Bestämning av läkemedelsrester i vatten med LC/MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_BEK_SPE_LVI-GC-MS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_BEK_SPE_LVI-GC-MS", "@language" : "sv" } ], "VocabularyConceptId" : "362882", "VocabularyId" : "27", "Identifier" : "SGS_BEK_SPE_LVI-GC-MS", "Label" : "SGS_BEK_SPE_LVI-GC-MS", "Definition" : "SGS-BEK-SPE-LVI-GC-MS Analysmetod SGS Analytics - Vattenundersökningar: Bestämning av bekämpningsmedel (bl.a. kinoxifen, bifenox och cypermetrin) i vatten. Efter fast-fas-extraktion (SPE) utförs analys med gaskromatograf med stor injektionsvolym (\"Large Volume Injection\", LVI) och masspektrometer (LVI-GC-MS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_BIOTA_PBDE", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_BIOTA_PBDE", "@language" : "sv" } ], "VocabularyConceptId" : "362883", "VocabularyId" : "27", "Identifier" : "SGS_BIOTA_PBDE", "Label" : "SGS_BIOTA_PBDE", "Definition" : "SGS-Biota Fisk/Skaldj-DIOXIN Analyspaket SGS Analytics Biota - Bestämning av 17 PCDD/PCDF samt WHO-PCDD/F-TEQ med GC-MS-MS (2,4,4’-TrBDE #28, 2,2’,4,4’-TeBDE #47, 2,2’,4,4’,5-PnBDE #99, 2,2’,4,4’,6-PnBDE #100, 2,2’,4,4’,5,6’-HxBDE #154, 2,2’,4,4’,5,5’-HxBDE #153, 2,2’,3,4,4’,5’,6-HpBDE #183, DekaBDE #209)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_BIOTA_PBDE_PAH", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_BIOTA_PBDE_PAH", "@language" : "sv" } ], "VocabularyConceptId" : "362884", "VocabularyId" : "27", "Identifier" : "SGS_BIOTA_PBDE_PAH", "Label" : "SGS_BIOTA_PBDE_PAH", "Definition" : "SGS-Biota-PBDE-PAH. Analyspaket SGS Analytics Biota - Bestämning av PBDE och PAH i biota. Prov extraheras med ultraljudsextraktion med ett opolärt lösningsmedel. Därefter sker olika reningssteg med diverse sorbenter (silica, NH2). Innan extraktion spikas proven med märkta internstandarder för att kompensera för förluster och matriseffekter (isotopspädning).Analys sker sedan med GC-APCI-MS-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_BIOTA_PFAS05", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_BIOTA_PFAS05", "@language" : "sv" } ], "VocabularyConceptId" : "362885", "VocabularyId" : "27", "Identifier" : "SGS_BIOTA_PFAS05", "Label" : "SGS_BIOTA_PFAS05", "Definition" : "SGS-Biota-PFAS05 Analyspaket SGS Analytics Biota - Bestämning av 21 PFAS med LC-MS-MS (Perfluorbutansulfonat (PFBS), Perfluorpentansulf, (PFPeS), Perfluorhexansulfonat(PFHxS), Perfluorheptansulfonat (PFHpS), PFOS linjär, PFOS grenad, PFOS total, Perfluorpentansyra (PFPeA), Perfluorhexansyra (PFHxA), Perfluorheptansyra (PFHpA), PFOA linjär, PFOA grenad, PFOA total, Fluortelomersulfonat., (4:2 FTS), Fluortelomersulfonat (6:2 FTS), Fluortelomersulfonat (8:2 FTS), Perfluorbutansyra (PFBA), Perfluornonansyra (PFNA), Perfluordekansyra (PFDA), Perfluorundekansyra (PFUnDA), Perfluordodekansyra (PFDoDA), Perfluoroktansulfonamid PFOSA, 7H-Dodekafluorheptansyra HPFHpA)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMLi_4", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMLi_4", "@language" : "sv" } ], "VocabularyConceptId" : "362886", "VocabularyId" : "27", "Identifier" : "SGS_KMLi_4", "Label" : "SGS_KMLi_4", "Definition" : "SGS KMLi-4 Bestämning av vattenhalt, askhalt och ICP i livsmedel och foder. Vattenhalt och askhalt bestäms gravimetriskt genom torkning vid 102-105°C respektive inaskning vid 550 ± 25°C. Baserad på NMKL (f.d. \"Nordisk Metodikkomité for Næringsmidler\", från 2022 ändrat till \"Nordic-Baltic Committee on Food Analysis\") Nr 23 Utgåva 3, 1991 - Vatten och aska. Gravimetrisk bestämning i kött och köttvaror", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_107", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_107", "@language" : "sv" } ], "VocabularyConceptId" : "362887", "VocabularyId" : "27", "Identifier" : "SGS_KMO_107", "Label" : "SGS_KMO_107", "Definition" : "SGS KMO-107: Analysmetod SGS Analytics - Kvantitativ bestämning av läkemedelsrester i vatten genom direktinjektion av 50 µl prov på vätskekromatograf med trippel kvadrupol masspektrometer (LC-QQQ)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_38", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_38", "@language" : "sv" } ], "VocabularyConceptId" : "362888", "VocabularyId" : "27", "Identifier" : "SGS_KMO_38", "Label" : "SGS_KMO_38", "Definition" : "SGS KMO-38 Analysmetod SGS Analytics - Bestämning av polyaromatiska kolväten (PAH), låga halter, i sediment. Prov extraheras med ultraljudsbad med cyklohexan/aceton och analyseras sedan med GC-ECD", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_65", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_65", "@language" : "sv" } ], "VocabularyConceptId" : "362889", "VocabularyId" : "27", "Identifier" : "SGS_KMO_65", "Label" : "SGS_KMO_65", "Definition" : "SGS KMO-65: Analysmetod SGS Analytics - Bestämning av polybromerade difenyletrar (PBDE) enligt EU:s vattendirektiv (2000/60/EG) samt dotterdirektiv (2008/105/EG), samt bestämning av hexabromcyklododekan (HBCD) och Tetrabrombisfenol A (TBBPA) i biota. Analys sker med GC-MS-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_66", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_66", "@language" : "sv" } ], "VocabularyConceptId" : "362890", "VocabularyId" : "27", "Identifier" : "SGS_KMO_66", "Label" : "SGS_KMO_66", "Definition" : "SGS KMO-66 Vattenundersökningar - Bestämning av klorparaffiner C10-C13 (SCCP) med (LVI)-GC/MS NCI med extraktion diklormetan", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_69_20", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_69_20", "@language" : "sv" } ], "VocabularyConceptId" : "362891", "VocabularyId" : "27", "Identifier" : "SGS_KMO_69_20", "Label" : "SGS_KMO_69_20", "Definition" : "SGS KMO-69: Analysmetod SGS Analytics - Upparbetning av förbränningsprover, vattenprover och fasta prover för bestämning av PCDD/F (polyklorerade dibensodioxiner och -furaner), PBDD/F (polybromerade dibensodioxiner och -furaner) och PCB (polyklorerade bifenyler) för vidare bestämning enligt metod SGS KMO-20. Kvantitativ bestämning med GC-MS med högupplösande masspektrometri eller med trippelkvadrupolteknik", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_82", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_82", "@language" : "sv" } ], "VocabularyConceptId" : "362892", "VocabularyId" : "27", "Identifier" : "SGS_KMO_82", "Label" : "SGS_KMO_82", "Definition" : "SGS KMO-82 Vattenundersökningar – Fenoler i Vattenmatriser med (LVI)-GC/MS NCI efter derivatisering", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_90", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_90", "@language" : "sv" } ], "VocabularyConceptId" : "362893", "VocabularyId" : "27", "Identifier" : "SGS_KMO_90", "Label" : "SGS_KMO_90", "Definition" : "SGS KMO-90 Vattenundersökningar – Bestämning av glyfosat och AMPA i vatten med on-line SPE och LC-QQQ", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_91", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_91", "@language" : "sv" } ], "VocabularyConceptId" : "362894", "VocabularyId" : "27", "Identifier" : "SGS_KMO_91", "Label" : "SGS_KMO_91", "Definition" : "SGS KMO-91 Vattenundersökningar - Bestämning av bekämpningsmedel i vatten och jord/sediment med on-line SPE och LC-QQQ", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_94", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_94", "@language" : "sv" } ], "VocabularyConceptId" : "362895", "VocabularyId" : "27", "Identifier" : "SGS_KMO_94", "Label" : "SGS_KMO_94", "Definition" : "SGS KMO-94: Analysmetod SGS Analytics - Bestämning av 16 PAH-föreingar, samt penta- och hexaklorbensen i biota. Extraktion sker med ultraljud följt av rening med fast fas-extraktion (SPE) med NH2-kolonn. Analysen sker med LVI-GC-EI-MS-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_96", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_96", "@language" : "sv" } ], "VocabularyConceptId" : "362896", "VocabularyId" : "27", "Identifier" : "SGS_KMO_96", "Label" : "SGS_KMO_96", "Definition" : "SGS KMO-96 Bestämning av bekämpningsmedel och bronopol i vatten och bronopol i sediment med direktinjektion och LC-QQQ. De flesta bekämpningsmedel som analyseras med LC-MS-MS saknar fastfas-upparbetning. Vattnet mäts upp direkt i vial. Tillsatser tillsätts i vialen, sedan analyseras provet med analysinstrumentet LC-QQQ. Det här gäller bla Atrazin, Diuron, Simazin, Isoproturon (BEK4) men även t.ex. 2,4-diklorfenoxisyra, 2,4-diklorprop, BAM, Bentazon, Bitertanol, Boskalid, Bronopol, Cyanazin, Desetylatrazin, Desetylterbutylazin, Desisopropylatrazin, Dimetoat, Etofumesat, Fluroxipyr, Imidakloprid, Klopyralid, Kloridazon, Kvinmerak, MCPA, Mekoprop, Metalaxyl, Metamitron, Metazaklor, Metribuzin, Metsulfuronmetyl, Pirimikarb, Propyzamid, Sulfosulfuron, Terbutylazin, Thifensulfuronmetyl, Tribenuronmetyl", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_99", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_99", "@language" : "sv" } ], "VocabularyConceptId" : "362897", "VocabularyId" : "27", "Identifier" : "SGS_KMO_99", "Label" : "SGS_KMO_99", "Definition" : "SGS KMO-99: Analysmetod SGS Analytics - Bestämning av per- och polyfluorerade föreningar (PFAS) i vatten, jord, biota, avfall (betong/asfalt), sediment och slam med LC-MS-MS. Fasta materialen bereds innan analys med en basisk metanolextraktion", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_KMO_dikofol", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_KMO_dikofol", "@language" : "sv" } ], "VocabularyConceptId" : "362898", "VocabularyId" : "27", "Identifier" : "SGS_KMO_dikofol", "Label" : "SGS_KMO_dikofol", "Definition" : "SGS KMO-Dikofol Vattenundersökningar - Bestämninmg av Dikofol genom vätske-vätske-extraktion och analys med gaskromatografi och tandemmasspektrometri, GC-MS-MS (liquid-liquid extraction with injection on GC-MS-MS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_MET_0973", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_MET_0973", "@language" : "sv" } ], "VocabularyConceptId" : "362899", "VocabularyId" : "27", "Identifier" : "SGS_MET_0973", "Label" : "SGS_MET_0973", "Definition" : "SGS Analytics analysmetod MET-0973 för bestämning av alkoholer. Vatten: Alkoholer analyseras direkt med HS-GC-MS efter tillsats av internstandard 2-metyl-2-butanol. Glykoler anrikas med SPE, ENVI-Carb, vilka elueras med diklormetan.Jord, slam, sediment: Fast material extraheras med vatten efter tillsats av internstandard 2-metyl-2-butanol. Följer därefter samma procedur som för vattenprov", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_NL_EOX", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_NL_EOX", "@language" : "sv" } ], "VocabularyConceptId" : "362900", "VocabularyId" : "27", "Identifier" : "SGS_NL_EOX", "Label" : "SGS_NL_EOX", "Definition" : "SGS NL EOX: SGS NL analysmetod för bestämning av extraherbara organiskt bundna halogener; F, Cl, Br. Extraktion sker med hexan vilken uppkoncentreras genom indunstning varefter extraktet analyseras med mikrocoulometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_NL_LVI-GC-MS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_NL_LVI-GC-MS", "@language" : "sv" } ], "VocabularyConceptId" : "362901", "VocabularyId" : "27", "Identifier" : "SGS_NL_LVI-GC-MS", "Label" : "SGS_NL_LVI-GC-MS", "Definition" : "SGS NL-LVI-GC-MS: Analysmetod SGS Analytics - Analys av klorerade pesticider. Lösningsmedelsextraktion och analys med gaskromatograf med stor injektionsvolym (\"Large Volume Injection\") och masspektrometer (LVI-GC-MS)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_PAH16", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_PAH16", "@language" : "sv" } ], "VocabularyConceptId" : "362902", "VocabularyId" : "27", "Identifier" : "SGS_PAH16", "Label" : "SGS_PAH16", "Definition" : "SGS-PAH 16 Vattenundersökningar - Bestämning av 16 PAH med GC-MS ((Naftalen, Acenaftylen, Acenaften, Fluoren, Fenantren, Antracen, Fluoranten, Pyren, Benso[a]antracen, Krysen/Trifenylen, Benso[b]fluoranten, Benso[k]fluoranten, Benso[a]pyren, Dibenso[a,h]antracen, Benso[ghi]perylen, Indeno[1,2,3-cd]pyren)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_PAH_SED", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_PAH_SED", "@language" : "sv" } ], "VocabularyConceptId" : "362903", "VocabularyId" : "27", "Identifier" : "SGS_PAH_SED", "Label" : "SGS_PAH_SED", "Definition" : "SGS Analytics analysmetod för PAH i sediment. Extraktion sker vanligtvis med mikrovågsassisterad extraktion (MAE) där hexan/aceton (1:1 v/v) används som lösningsmedel. Innan extraktion tillsätts isotopmärkta standarder för att kompensera för eventuella förluster under provets gång. Kraftigt förorenade extrakt renas med SPE (aminopropyl). Analys sker med GC-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_SIS_CEN_TR_16998_2016_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_SIS_CEN_TR_16998_2016_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362904", "VocabularyId" : "27", "Identifier" : "SGS_SIS_CEN_TR_16998_2016_modifierad", "Label" : "SGS_SIS_CEN_TR_16998_2016_modifierad", "Definition" : "SGS Analytics analys enligt SIS-CEN/TR 16998:2016 (modifierad). Utomhusluft - Rapport om nitro- och oxy-PAH; - ursprung, toxicitet, halter och mätmetoder. Fast material extraheras, efter tillsats av isotopmärkta OxyPAH som internstandard, med en mix av aceton/hexan med sonikering, MAE eller soxhlet. Extrakt torkas med natriumsulfat och indunstas. Bestämning sker med GC-MS alt. GC-MS-MS", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_STD_MET_1998_20_4500_C_D_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_STD_MET_1998_20_4500_C_D_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362905", "VocabularyId" : "27", "Identifier" : "SGS_STD_MET_1998_20_4500_C_D_modifierad", "Label" : "SGS_STD_MET_1998_20_4500_C_D_modifierad", "Definition" : "SGS Analytics Standard Methods 1998 utgåva 20, metod 4500-C,D (modifierad) efter metod 941003 från Limnologiska institutionen, SLU, Uppsala. Vattenundersökningar - Bestämning av molybdatreaktivt kisel vilket analyserar mängden löst kisel. Prover tillsätts reagens och analyseras med spektrofotometer. Prover t.o.m. 2022-01-31", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_STD_MET_2017_23_4500_SiO2_C_D_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_STD_MET_2017_23_4500_SiO2_C_D_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362906", "VocabularyId" : "27", "Identifier" : "SGS_STD_MET_2017_23_4500_SiO2_C_D_modifierad", "Label" : "SGS_STD_MET_2017_23_4500_SiO2_C_D_modifierad", "Definition" : "SGS Analytics Standard Methods 2017 utgåva 23, metod 4500-SiO2 C, D (modifierad) efter metod 941003 från Limnologiska institutionen, SLU, Uppsala. Vattenundersökningar - Bestämning av molybdatreaktivt kisel vilket analyserar mängden löst kisel. Prover tillsätts reagens och analyseras med spektrofotometer. Prover från 2022-02-01", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SGS_TOPASSAY_PFAS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SGS_TOPASSAY_PFAS", "@language" : "sv" } ], "VocabularyConceptId" : "362907", "VocabularyId" : "27", "Identifier" : "SGS_TOPASSAY_PFAS", "Label" : "SGS_TOPASSAY_PFAS", "Definition" : "SGS Analytics TOP (Total Oxidisable Precursors)-assay för PFAS. Bestämning av PFAS i vatten före och efter oxidation med kaliumperoxid och efterföljande analys med LC-QQQ", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SIS_CEN_TR_16192_2020", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SIS_CEN_TR_16192_2020", "@language" : "sv" } ], "VocabularyConceptId" : "362908", "VocabularyId" : "27", "Identifier" : "SIS_CEN_TR_16192_2020", "Label" : "SIS_CEN_TR_16192_2020", "Definition" : "SIS-CEN/TR 16192:2020 Karaktärisering av avfall - Analys av lakvatten", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SIS_CEN_TS_16183_2013", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SIS_CEN_TS_16183_2013", "@language" : "sv" } ], "VocabularyConceptId" : "362909", "VocabularyId" : "27", "Identifier" : "SIS_CEN_TS_16183_2013", "Label" : "SIS_CEN_TS_16183_2013", "Definition" : "SIS-CEN/TS 16183:2013 Sludge, treated biowaste and soil – Determination of selected phthalates using capillary gas chromatography with mass spectrometric detection (GC-MS). Publicerad/Published: 2013-09-12Utgåva/Edition: 1, Språk/Language: engelska/English, CS: 13.030.01", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SIS_TK_535_N_012", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SIS_TK_535_N_012", "@language" : "sv" } ], "VocabularyConceptId" : "362910", "VocabularyId" : "27", "Identifier" : "SIS_TK_535_N_012", "Label" : "SIS_TK_535_N_012", "Definition" : "SIS/TK 535 N 012 Instruktion för analys av fraktionen Aromater >C16-C35", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLU-AQUA_ALGTOX", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLU-AQUA_ALGTOX", "@language" : "sv" } ], "VocabularyConceptId" : "362911", "VocabularyId" : "27", "Identifier" : "SLU-AQUA_ALGTOX", "Label" : "SLU-AQUA_ALGTOX", "Definition" : "SLU AQUA analysis of algal toxins. Extraction with mixture of iso-hexane, iso-propanol, and diethyl ether (3:5:1), 25 mL) was followed by derivatisation. A tetrabutylammonium (TBA) carbonate buffer (1.5 mL) made by dissolving sodium carbonate (Na2CO3; 4.24 g) and tetrabutyl ammonium hydrogen sulfate (TBAHSO4; 6.8 g) in water (100 mL) was added to the sample. Acetic acid anhydride (50 µL) was then added and the sample was mixed for 1 min, by shaking by hand. This process was repeated once more with an additional portion of acetic acid anhydride (50 µL). When the reaction was finalised, the organic solvent was isolated and reduced to 100 µL under a stream of nitrogen gas prior to instrumental analysis by MS-ENCI with methane as buffer gas", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLU_HG", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLU_HG", "@language" : "sv" } ], "VocabularyConceptId" : "362912", "VocabularyId" : "27", "Identifier" : "SLU_HG", "Label" : "SLU_HG", "Definition" : "SLU-Hg analysis. The analyses of mercury were done according to May and Stoeppler, and Lindsted and Skare using a double-beam spectrophotometer. May, K. & Stoeppler, M. Pretreatment studies with biological and environmental materials. Fresenius J Anal Chem 317, 248–251 (1984). Lindsted, G. & Skare, I. Microdetermination of mercury in biological samples. Analyst 96, 223–229 (1971)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLU_METALLER_AAS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLU_METALLER_AAS", "@language" : "sv" } ], "VocabularyConceptId" : "362913", "VocabularyId" : "27", "Identifier" : "SLU_METALLER_AAS", "Label" : "SLU_METALLER_AAS", "Definition" : "SLU-Metallanalys 1989-01 – 1995-07. Vid bestämningen av metaller skedde en direkt injicering av surgjort ofiltrerat vattenprov (0.5 ml HNO3/100 ml, SS 02 81 83). Analysen utfördes med en Philips PU 9200 Atomabsorptionsspektrometer med grafitugn och med en Philips PU 9390 elektrotermisk atomiserare och autosampler (The quantification of metals was conducted on a Philips PU 9200 Atomic Absorption Spectrophotometer with a graphite furnace and with a Philips PU 9390 electrothermal atomizer and autosampler) Enligt: Borg, H., Edin, A. & Sköld, E. Determination of metals in fish livers by flameless atomic absorption spectroscopy. Water Res (1981)", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLU_METALLER_ICP-MS", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLU_METALLER_ICP-MS", "@language" : "sv" } ], "VocabularyConceptId" : "362914", "VocabularyId" : "27", "Identifier" : "SLU_METALLER_ICP-MS", "Label" : "SLU_METALLER_ICP-MS", "Definition" : "SLU-Metallanalys 1995-08 – 2007-08. Vid bestämningen av metaller skedde en direkt injicering av surgjort ofiltrerat vattenprov (0.5 ml HNO3/100 ml). Analysen utfördes med en Perkin-Elmer ELAN 6000 ICP-MS masspektrometrer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLU_OMK_51", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLU_OMK_51", "@language" : "sv" } ], "VocabularyConceptId" : "362915", "VocabularyId" : "27", "Identifier" : "SLU_OMK_51", "Label" : "SLU_OMK_51", "Definition" : "SLU-OMK 51. Multimetod för analys av opolära och semipolära pesticider i vatten. 500 g prov tas ut och internstandard tillsätts före vätske-vätske-extraktion med diklormetan. Organfasen torkas med natriumsulfat och koncentreras till 1 ml slutvolym. Extrakten analyseras med gaskromatograf med massspektrometrisk bestämning (GC-MS och GC-MS-MS) och med en kapillärkolonn för MS-detektor, längd 30 m, i.d. 0,25 mm, fastjocklek 0,25 µm (t.ex. HP-5MS). Beräkningar av koncentrationer (ca 32 analyter) görs med utvärderingsprogrammet MassHunter 10. Kalibreringskurvor med standard-mixar av certifierade substanser används vid beräkningarna", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLU_OMK_57", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLU_OMK_57", "@language" : "sv" } ], "VocabularyConceptId" : "362916", "VocabularyId" : "27", "Identifier" : "SLU_OMK_57", "Label" : "SLU_OMK_57", "Definition" : "SLU-OMK 57. Multimetod för analys av olika polära och semipolära analyter i yt-, regn- och grundvatten. pH i provet justeras till cirka pH 5,0. Till provet sätts 2% metanol och internstandard före filtrering (0,2 µm sprutfilter, regenererad cellulosa) innan analys. Automatisk koncentrering och analys med vätskekromatograf med masspektrometrisk bestämning (LC-MS-MS). Förkoncentreringskolonner (typ Strata C18, 20 µm 20x2 mm, Strata X, 25 µm 20x2 mm i serie), analyskolonn för reversed phase (ex Eclipse Plus C18, 3,0x100 mm). HPLC (Agilent 1260 eller 1290) och LC-MS-MS med elektrospray-interface, ES+, (Agilent 6470). Beräkningar av koncentrationer (ca 110 analyter) görs med utvärderingsprogrammet MassHunter 10. Kalibreringskurvor med standard-mixar av certifierade substanser används vid beräkningarna", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLU_OMK_58", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLU_OMK_58", "@language" : "sv" } ], "VocabularyConceptId" : "362917", "VocabularyId" : "27", "Identifier" : "SLU_OMK_58", "Label" : "SLU_OMK_58", "Definition" : "SLU-OMK 58. Metod för analys av fenoxisyror och andra sura analyter i vatten med LC-MS-MS. pH i provet justeras till cirka pH 2,5 med myrsyra. Till provet sätts 2% metanol och internstandard före filtrering (0,2 µm sprutfilter, regenererad cellulosa) innan analys. Automatisk koncentrering och analys med vätskekromatograf med masspektrometrisk bestämning (LC-MS-MS). Förkoncentreringskolonner (t.ex. Spark PLRP, 20 µm 20x2 mm), analyskolonn för reversed phase (ex Eclipse Plus C18, 3,0x100 mm). HPLC (Agilent 1260 eller 1290) och LC-MS-MS med elektrospray-interface, ES-, (Agilent 6470). Beräkningar av koncentrationer (ca 20 analyter) görs med utvärderingsprogrammet MassHunter 10. 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Treated extract was evaporated under nitrogen stream until dryness and methanol was added. Aliquots of the final extracts were injected on a liquid chromatography (LC) system coupled to a tandem mass spectrometer", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "SLV_K2_M261_F3_modifierad", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "SLV_K2_M261_F3_modifierad", "@language" : "sv" } ], "VocabularyConceptId" : "362919", "VocabularyId" : "27", "Identifier" : "SLV_K2_M261_F3_modifierad", "Label" : "SLV_K2_M261_F3_modifierad", "Definition" : "SLV K2-m261-f3 (modifierad) (Livsmedelsverket). Bestämning av PAH i livsmedel. 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The extraction method is described by Wiberg and co-workers [Wiberg et al., 1998], the clean-up method by Danielsson and co-workers [Danielsson et al., 2005], and the instrumental analysis (GC-HRMS) by Liljelind and co-workers [Liljelind et al., 2003]. The laboratory participates in the annual FOOD intercalibration rounds, including laboratory reference material (salmon tissue) with each set of samples", "Notation" : null, "Status" : "Valid", "StatusModifiedDate" : "2026-03-13", "AcceptedDate" : "2026-03-13", "NotAcceptedDate" : null, "broader" : [ ], "narrower" : [ ], "skos:editorialNote" : [ ] }, { "@id" : "UMU_KEM_BEK_SED", "@type" : "skos:Concept", "prefLabel" : [ { "@value" : "UMU_KEM_BEK_SED", "@language" : "sv" } ], "VocabularyConceptId" : "363054", "VocabularyId" : "27", "Identifier" : "UMU_KEM_BEK_SED", "Label" : "UMU_KEM_BEK_SED", "Definition" : "UMU-KEM-BEK: Umeå universitet, Kemiska institutionen. Sedimentundersökningar - Bestämning av bekämpningsmedel i sediment. 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