-
Je něco špatně v tomto záznamu ?
Unraveling the Relationship between the Concentrations of Hydrophobic Organic Contaminants in Freshwater Fish of Different Trophic Levels and Water Using Passive Sampling
F. Smedes, J. Sobotka, TP. Rusina, P. Fialová, P. Carlsson, R. Kopp, B. Vrana,
Jazyk angličtina Země Spojené státy americké
Typ dokumentu časopisecké články, práce podpořená grantem
PubMed
32551598
DOI
10.1021/acs.est.9b07821
Knihovny.cz E-zdroje
- MeSH
- chemické látky znečišťující vodu * analýza MeSH
- monitorování životního prostředí * MeSH
- potravní řetězec MeSH
- ryby MeSH
- sladká voda MeSH
- voda MeSH
- zvířata MeSH
- Check Tag
- zvířata MeSH
- Publikační typ
- časopisecké články MeSH
- práce podpořená grantem MeSH
- Geografické názvy
- Česká republika MeSH
- Slovenská republika MeSH
The concentrations of hydrophobic organic compounds (HOCs) in aquatic biota are used for compliance, as well as time and spatial trend monitoring in the aqueous environment (European Union water framework directive, OSPAR). Because of trophic magnification in the food chain, the thermodynamic levels of HOCs, for example, polychlorinated biphenyl congeners, dichlorodiphenyltrichloroethane, and brominated diphenyl ether congeners, in higher trophic level (TL) organisms are expected to be strongly elevated above those in water. This work compares lipid-based concentrations at equilibrium with the water phase derived from aqueous passive sampling (CL⇌water) with the lipid-based concentrations in fillet and liver of fish (CL) at different TLs for three water bodies in the Czech Republic and Slovakia. The CL values of HOCs in fish were near CL⇌water, only after trophic magnification up to TL = 4. For fish at lower TL, CL progressively decreased relative to CL⇌water as KOW of HOCs increased above 106. The CL value decreasing toward the bottom of the food chain suggests nonequilibrium for primary producers (algae), which is in agreement with modeling passive HOC uptake by algae. Because trophic magnification and the resulting CL in fish exhibit large natural variability, CL⇌water is a viable alternative for monitoring HOCs using fish, showing a twofold lower confidence range and requiring less samples.
Citace poskytuje Crossref.org
- 000
- 00000naa a2200000 a 4500
- 001
- bmc20028022
- 003
- CZ-PrNML
- 005
- 20210114152821.0
- 007
- ta
- 008
- 210105s2020 xxu f 000 0|eng||
- 009
- AR
- 024 7_
- $a 10.1021/acs.est.9b07821 $2 doi
- 035 __
- $a (PubMed)32551598
- 040 __
- $a ABA008 $b cze $d ABA008 $e AACR2
- 041 0_
- $a eng
- 044 __
- $a xxu
- 100 1_
- $a Smedes, Foppe $u Faculty of Science, Centre RECETOX, Masaryk University, Kamenice 753/5, 625 00 Brno, Czech Republic.
- 245 10
- $a Unraveling the Relationship between the Concentrations of Hydrophobic Organic Contaminants in Freshwater Fish of Different Trophic Levels and Water Using Passive Sampling / $c F. Smedes, J. Sobotka, TP. Rusina, P. Fialová, P. Carlsson, R. Kopp, B. Vrana,
- 520 9_
- $a The concentrations of hydrophobic organic compounds (HOCs) in aquatic biota are used for compliance, as well as time and spatial trend monitoring in the aqueous environment (European Union water framework directive, OSPAR). Because of trophic magnification in the food chain, the thermodynamic levels of HOCs, for example, polychlorinated biphenyl congeners, dichlorodiphenyltrichloroethane, and brominated diphenyl ether congeners, in higher trophic level (TL) organisms are expected to be strongly elevated above those in water. This work compares lipid-based concentrations at equilibrium with the water phase derived from aqueous passive sampling (CL⇌water) with the lipid-based concentrations in fillet and liver of fish (CL) at different TLs for three water bodies in the Czech Republic and Slovakia. The CL values of HOCs in fish were near CL⇌water, only after trophic magnification up to TL = 4. For fish at lower TL, CL progressively decreased relative to CL⇌water as KOW of HOCs increased above 106. The CL value decreasing toward the bottom of the food chain suggests nonequilibrium for primary producers (algae), which is in agreement with modeling passive HOC uptake by algae. Because trophic magnification and the resulting CL in fish exhibit large natural variability, CL⇌water is a viable alternative for monitoring HOCs using fish, showing a twofold lower confidence range and requiring less samples.
- 650 _2
- $a zvířata $7 D000818
- 650 12
- $a monitorování životního prostředí $7 D004784
- 650 _2
- $a ryby $7 D005399
- 650 _2
- $a potravní řetězec $7 D020387
- 650 _2
- $a sladká voda $7 D005618
- 650 _2
- $a voda $7 D014867
- 650 12
- $a chemické látky znečišťující vodu $x analýza $7 D014874
- 651 _2
- $a Česká republika $7 D018153
- 651 _2
- $a Slovenská republika $7 D018154
- 655 _2
- $a časopisecké články $7 D016428
- 655 _2
- $a práce podpořená grantem $7 D013485
- 700 1_
- $a Sobotka, Jaromír $u Faculty of Science, Centre RECETOX, Masaryk University, Kamenice 753/5, 625 00 Brno, Czech Republic.
- 700 1_
- $a Rusina, Tatsiana P $u Faculty of Science, Centre RECETOX, Masaryk University, Kamenice 753/5, 625 00 Brno, Czech Republic.
- 700 1_
- $a Fialová, Pavla $u Faculty of Science, Centre RECETOX, Masaryk University, Kamenice 753/5, 625 00 Brno, Czech Republic.
- 700 1_
- $a Carlsson, Pernilla $u Faculty of Science, Centre RECETOX, Masaryk University, Kamenice 753/5, 625 00 Brno, Czech Republic. Fram Centre, Norwegian Institute for Water Research (NIVA), Hjalmar Johansen Gate 14, 9007 Tromsø, Norway.
- 700 1_
- $a Kopp, Radovan $u Faculty of AgriSciences, Department of Zoology, Fisheries, Hydrobiology and Apiculture (FA), Mendel University in Brno, Zemědělská 1, 61300 Brno, Czech Republic.
- 700 1_
- $a Vrana, Branislav $u Faculty of Science, Centre RECETOX, Masaryk University, Kamenice 753/5, 625 00 Brno, Czech Republic.
- 773 0_
- $w MED00001559 $t Environmental science & technology $x 1520-5851 $g Roč. 54, č. 13 (2020), s. 7942-7951
- 856 41
- $u https://pubmed.ncbi.nlm.nih.gov/32551598 $y Pubmed
- 910 __
- $a ABA008 $b sig $c sign $y a $z 0
- 990 __
- $a 20210105 $b ABA008
- 991 __
- $a 20210114152818 $b ABA008
- 999 __
- $a ok $b bmc $g 1608357 $s 1119202
- BAS __
- $a 3
- BAS __
- $a PreBMC
- BMC __
- $a 2020 $b 54 $c 13 $d 7942-7951 $e 20200618 $i 1520-5851 $m Environmental science & technology $n Environ Sci Technol $x MED00001559
- LZP __
- $a Pubmed-20210105