Analysis of biota
IVL Swedish Environmental Research Institute analyzes emissions of water pollutants and how they are absorbed and affect fish, mussels and more biota.
Through the close connection that exists at IVL between research and access to our own analysis laboratories, we can offer complete solutions that cover the entire chain from sampling plans to advice for action plans.
The analyzes are performed in our advanced laboratories. Many of our measurement and analysis methods are accredited by Swedac
External link, opens in new window. according to SS-EN ISO / IEC 17025: 2018. For other methods, we work based on corresponding quality routines.
Hire IVL for:
- Determination of elemental analysis, including mercury, PAH, PFAS, drug residues, pesticides, flame retardants, and plasticizers in plastic materials
- Preparation of test plans
- Carrying out sampling and sample fishing
- Analyzes, risk assessments and advice for action plans
Contact
We would like to know more about your specific needs for lab services. Fill in the form below and we will contact you shortly. Please note that IVL does not perform analyses for private individuals.
Ämnen vi mäter
Uppgifterna nedan om mätområde och mätosäkerhet är ungefärliga. För aktuella uppgifter kontakta kontaktpersonen ovan.
OORGANISKA ANALYSER | ||||||
|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad |
kvicksilver, totalt i fasta material | CVAFS | ng/g | 0.03 | 0.1 | 9% | ja |
metylkvicksilver i fasta material | CVAFS | ng/g | 0.02 | 0.06 | 13% | nej |
metylkvicksilver | CVAFS | ng/g | 0.02 | 0.06 | nej | |
Al | ICP-MS | ng/prov | 10 | 30 | 50% | ja |
As | ICP-MS | ng/prov | 0,005 | 0,015 | 25% | ja |
Pb | ICP-MS | ng/prov | 0,006 | 0,02 | 25% | ja |
Cd | ICP-MS | ng/prov | 0,001 | 0,003 | 15% | ja |
Co | ICP-MS | ng/prov | 0,003 | 0,006 | 20% | ja |
Cu | ICP-MS | ng/prov | 0,03 | 0,01 | 20% | ja |
Cr | ICP-MS | ng/prov | 0,3 | 0,1 | 35% | ja |
Fe | ICP-MS | ng/prov | 2,0 | 6,0 | 40% | ja |
Hg | ICP-MS | ng/prov | 0,003 | 0,01 | 30% | ja |
Mn | ICP-MS | ng/prov | 0,04 | 0,12 | 20% | ja |
Mo | ICP-MS | ng/prov | 0,007 | 0,025 | 50% | ja |
Ni | ICP-MS | ng/prov | 0,5 | 0,17 | 20% | ja |
V | ICP-MS | ng/prov | 0,009 | 0,03 | 20% | ja |
Zn | ICP-MS | ng/prov | 0,4 | 1,2 | 20% | ja |
Sb | ICP-MS | ng/prov | nej | |||
ORGANISKA ANALYSER | ||||||
|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad |
PCB 28 | PCB på GC-EC | ng/prov | 0.15 | 0.4 | 40% | ja |
PCB 52 | PCB på GC-EC | ng/prov | 0.1 | 0.4 | 30% | ja |
PCB 101 | PCB på GC-EC | ng/prov | 0.1 | 0.4 | 30% | ja |
PCB 118 | PCB på GC-EC | ng/prov | 0.1 | 0.3 | 30% | ja |
PCB 138 | PCB på GC-EC | ng/prov | 0.05 | 0.3 | 30% | ja |
PCB 153 | PCB på GC-EC | ng/prov | 0.1 | 0.3 | 30% | ja |
PCB 180 | PCB på GC-EC | ng/prov | 0.05 | 0.3 | 30% | ja |
Antracen | PAH, HPLC-fluorescens | ng/prov | 0.04 | 0.15 | 100% | ja |
Benso(a)-antracen | PAH, HPLC-fluorescens | ng/prov | 0.2 | 0.6 | 40% | ja |
Benso(a)-pyren | PAH, HPLC-fluorescens | ng/prov | 0.15 | 0.5 | 30% | ja |
Benso(b)-flouranten | PAH, HPLC-fluorescens | ng/prov | 0.2 | 0.7 | 30% | ja |
Benso(ghi)-perylen | PAH, HPLC-fluorescens | ng/prov | 0.3 | 1 | 40% | ja |
Benso(k)-flouranten | PAH, HPLC-fluorescens | ng/prov | 0.05 | 0.4 | 20% | ja |
Krysen | PAH, HPLC-fluorescens | ng/prov | 0.15 | 0.55 | 30% | ja |
Dibenso(a,h)-antracen | PAH, HPLC-fluorescens | ng/prov | 0.2 | 0.5 | 30% | ja |
Fenantren | PAH, HPLC-fluorescens | ng/prov | 0,6 | 2 | 50% | ja |
Fluoranten | PAH, HPLC-fluorescens | ng/prov | 0.4 | 1.2 | 40% | ja |
Indeno(cd)-pyren | PAH, HPLC-fluorescens | ng/prov | 0.6 | 2 | 40% | ja |
Pyren | PAH, HPLC-fluorescens | ng/prov | 0.5 | 1.3 | 30% | ja |
Hormoner | ||||||
|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad |
Estrone | fiskgalla, GC-MS | ng/g våtvikt | 1 | 3 | - | Nej |
β-Estradiol | fiskgalla ,GC-MS | ng/g våtvikt | 1 | 3 | - | Nej |
Ethynylestradiol | fiskgalla, GC-MS | ng/g våtvikt | 1 | 3 | - | Nej |
Perfluorerade föreningar | ||||||
|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad |
Perfluorobutansulfonat (PFBS) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluorohexansulfonat (PFHxS) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluoroktansulfonat (PFOS) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluorodekansulfonat (PFDS) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluorooktansulfonamid (PFOSA) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
6:2 FTS | ng/g vv | 0.5 | 1.5 | ca ±20% | nej | |
Perfluoropentansyra (PFPeA) | ng/g vv | 0.5 | 1.5 | ca ±20% | nej | |
Perfluorohexansyra (PFHxA) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluoroheptansyra (PFHpA) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluorooktansyra (PFOA) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluorononansyra (PFNA) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluorodekansyra (PFDA) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Perfluoroundekansyra (PFUnDA) | ng/g vv | 0.2 | 0.6 | ca ±20% | nej | |
Organiska tennföreningar | |||||||
|---|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad | |
Monobutyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Dibutyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Tributyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Monofenyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Difenyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Trifenyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Monooktyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Dioktyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | ||
Organiska tennföreningar | ||||||
|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad |
Monobutyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | |
Dibutyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | |
Tributyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | |
Monofenyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | |
Difenyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | |
Trifenyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | |
Monooktyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej | |
Dioktyltenn | ng/g WW | <0.5 | <1.5 | 30%. | nej |
Ftalater | ||||||
|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad |
DIBP | ng/g WW | 4 | 30%. | nej | ||
DBP | ng/g WW | 4 | 30%. | nej | ||
BBP | ng/g WW | 6 | 30%. | nej | ||
DEHP | ng/g WW | 6 | 30%. | nej | ||
DINP | ng/g WW | 44 | 30%. | nej | ||
DIDP | ng/g WW | 77 | 30%. | nej | ||
DOP | ng/g WW | 1 | 30%. | nej | ||
Organiska fosfatestrar | ||||||
|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad |
TIBP = tris(iso-butyl)fosfat | ng/g WW | 0.2 | 30%. | nej | ||
TBP = tributylfosfat | ng/g WW | 0.2 | 30%. | nej | ||
TCEP = tris(2-kloretyl)fosfat | ng/g WW | 2 | 30%. | nej | ||
TCPP = tris(2-klor-iso-propyl)fosfat | ng/g WW | 2 | 30%. | nej | ||
DBPhP = di-butylfenylfosfat | ng/g WW | 0.3 | 30%. | nej | ||
DPhBP = butyldifenylfosfat | ng/g WW | 1 | 30%. | nej | ||
TDCPP = tris(1,3-diklor-iso-propyl)fosfat | ng/g WW | 2 | 30%. | nej | ||
TBEP = tris(2-butoxyetyl)fosfat | ng/g WW | 1 | 30%. | nej | ||
TPhP = trifenylfosfat | ng/g WW | 0.4 | 30%. | nej | ||
EHDPP = 2-etylhexyl-di-fenylfosfat | ng/g WW | 0.2 | 30%. | nej | ||
TEHP = tris(2-etylhexyl)fosfat | ng/g WW | 0.1 | 30%. | nej | ||
ToCP = tris(o-kresol)fosfat | ng/g WW | 1 | 30%. | nej | ||
TCP = trikresylfosfat | ng/g WW | 1 | 30%. | nej | ||
Fenoler | |||||||
|---|---|---|---|---|---|---|---|
Analyt | Metod | Enhet | LOD | LOQ | Mätosäkerhet | Ackrediterad | |
4-t-oktylfenol | ng/g vv | 0.1 | 30%. | nej | |||
4-iso-nonylfenol | ng/g vv | 4 | 30%. | nej | |||
BPA | ng/g vv | 1 | 30%. | nej | |||
2,4-dibromfenol | ng/g vv | 1 | 30%. | nej | |||
2,4,6-Tribromfenol | ng/g vv | 0.4 | 30%. | nej | |||
Tetrabrombisfenol A | ng/g vv | 6 | 40%. | nej | |||
Pentaklorfenol | ng/g vv | 0.3 | 30%. | nej | |||
Triklosan | ng/g vv | 0.3 | 30%. | nej |