-
Je něco špatně v tomto záznamu ?
Avian high-dose toxicity of cyanobacterial biomass
J. Kral, J. Pikula, H. Bandouchova, V. Damkova, K. Hilscherova, J. Misik, L. Novotny, K. Ondracek, J. Osickova, V. Mlcakova, M. Pohanka, H. Skochova, F. Vitula, F. Treml,
Jazyk angličtina Země Švédsko
Typ dokumentu časopisecké články, práce podpořená grantem
- MeSH
- bakteriální toxiny toxicita MeSH
- biomasa MeSH
- Coturnix * MeSH
- hepatocyty účinky léků patologie MeSH
- karcinogeny toxicita MeSH
- LD50 MeSH
- lékové postižení jater epidemiologie patologie MeSH
- mikrocystiny toxicita MeSH
- mořské toxiny toxicita MeSH
- náhodné rozdělení MeSH
- rizikové faktory MeSH
- sinice chemie MeSH
- tělesná hmotnost MeSH
- velikost orgánu MeSH
- vztah mezi dávkou a účinkem léčiva MeSH
- zvířata MeSH
- Check Tag
- mužské pohlaví MeSH
- zvířata MeSH
- Publikační typ
- časopisecké články MeSH
- práce podpořená grantem MeSH
OBJECTIVES: Previous studies using oral administration of environmentally relevant doses of cyanobacterial biomass containing microcystins (MCs) induced only sub-lethal effects in experimental birds. Therefore, the objective of this study was to obtain data on avian high-dose toxicity of MCs and compute LD50, if possible, following the natural oral route of administration. DESIGN: Responses of birds to single high-dose exposure to MCs were evaluated in fourteen-day old Japanese quail males (Coturnix coturnix japonica) with average body weight of 50 g which were randomly divided into five groups. Birds from four experimental groups were administered 7.5 ml of cyanobacterial biomass suspension containing increasing MCs quantities of 2500, 5000, 10000, and 20000 µg/kg using oral gavage. Controls received an equal dose of drinking water instead of the test substance. Birds were observed for clinical signs of acute toxicity. Survivors were killed on day 5 to obtain body and liver weights. A five-grade semi-quantitative system for histopathological liver damage scoring was used to compare cyanobacterial-biomass-exposed birds against controls. RESULTS: No mortality occurred during the period of five days post exposure in both control and MCs-exposed groups and this high-dose experiment failed to provide data to compute the LD50. Nevertheless, marked sub-lethal effects were recognised in the damage of liver that included dose-dependent changes in the body/liver ratios and morphological changes ranging from mild vacuolar dystrophy to focal liver necroses in the highest exposure group. Hepatic lesions were mainly observed in the pericentral area of the liver. CONCLUSIONS: Though maximum cyanobacterial biomass dose rates that could be administered to birds of the size were used in the present experiment and more pronounced hepatic lesions than after exposure to environmentally relevant doses were observed, birds would probably have survived unless killed for histopathology on day 5 of exposure. These results provide support to previously reported data on sub-lethal effects following exposure to cyanobacterial biomass containing MCs in birds and mortality occurring only in birds under combined action with other stressors.
- 000
- 00000naa a2200000 a 4500
- 001
- bmc13023986
- 003
- CZ-PrNML
- 005
- 20131002122716.0
- 007
- ta
- 008
- 130703s2012 sw f 000 0|eng||
- 009
- AR
- 035 __
- $a (PubMed)23353861
- 040 __
- $a ABA008 $b cze $d ABA008 $e AACR2
- 041 0_
- $a eng
- 044 __
- $a sw
- 100 1_
- $a Kral, Jiri $u Department of Veterinary Ecology and Environmental Protection, University of Veterinary and Pharmaceutical Sciences Brno, Czech Republic.
- 245 10
- $a Avian high-dose toxicity of cyanobacterial biomass / $c J. Kral, J. Pikula, H. Bandouchova, V. Damkova, K. Hilscherova, J. Misik, L. Novotny, K. Ondracek, J. Osickova, V. Mlcakova, M. Pohanka, H. Skochova, F. Vitula, F. Treml,
- 520 9_
- $a OBJECTIVES: Previous studies using oral administration of environmentally relevant doses of cyanobacterial biomass containing microcystins (MCs) induced only sub-lethal effects in experimental birds. Therefore, the objective of this study was to obtain data on avian high-dose toxicity of MCs and compute LD50, if possible, following the natural oral route of administration. DESIGN: Responses of birds to single high-dose exposure to MCs were evaluated in fourteen-day old Japanese quail males (Coturnix coturnix japonica) with average body weight of 50 g which were randomly divided into five groups. Birds from four experimental groups were administered 7.5 ml of cyanobacterial biomass suspension containing increasing MCs quantities of 2500, 5000, 10000, and 20000 µg/kg using oral gavage. Controls received an equal dose of drinking water instead of the test substance. Birds were observed for clinical signs of acute toxicity. Survivors were killed on day 5 to obtain body and liver weights. A five-grade semi-quantitative system for histopathological liver damage scoring was used to compare cyanobacterial-biomass-exposed birds against controls. RESULTS: No mortality occurred during the period of five days post exposure in both control and MCs-exposed groups and this high-dose experiment failed to provide data to compute the LD50. Nevertheless, marked sub-lethal effects were recognised in the damage of liver that included dose-dependent changes in the body/liver ratios and morphological changes ranging from mild vacuolar dystrophy to focal liver necroses in the highest exposure group. Hepatic lesions were mainly observed in the pericentral area of the liver. CONCLUSIONS: Though maximum cyanobacterial biomass dose rates that could be administered to birds of the size were used in the present experiment and more pronounced hepatic lesions than after exposure to environmentally relevant doses were observed, birds would probably have survived unless killed for histopathology on day 5 of exposure. These results provide support to previously reported data on sub-lethal effects following exposure to cyanobacterial biomass containing MCs in birds and mortality occurring only in birds under combined action with other stressors.
- 650 _2
- $a zvířata $7 D000818
- 650 _2
- $a bakteriální toxiny $x toxicita $7 D001427
- 650 _2
- $a biomasa $7 D018533
- 650 _2
- $a tělesná hmotnost $7 D001835
- 650 _2
- $a karcinogeny $x toxicita $7 D002273
- 650 12
- $a Coturnix $7 D003370
- 650 _2
- $a sinice $x chemie $7 D000458
- 650 _2
- $a vztah mezi dávkou a účinkem léčiva $7 D004305
- 650 _2
- $a lékové postižení jater $x epidemiologie $x patologie $7 D056486
- 650 _2
- $a hepatocyty $x účinky léků $x patologie $7 D022781
- 650 _2
- $a LD50 $7 D007928
- 650 _2
- $a mužské pohlaví $7 D008297
- 650 _2
- $a mořské toxiny $x toxicita $7 D008387
- 650 _2
- $a mikrocystiny $x toxicita $7 D052998
- 650 _2
- $a velikost orgánu $7 D009929
- 650 _2
- $a náhodné rozdělení $7 D011897
- 650 _2
- $a rizikové faktory $7 D012307
- 655 _2
- $a časopisecké články $7 D016428
- 655 _2
- $a práce podpořená grantem $7 D013485
- 700 1_
- $a Pikula, Jiri $u -
- 700 1_
- $a Bandouchova, Hana $u -
- 700 1_
- $a Damkova, Veronika $u -
- 700 1_
- $a Hilscherova, Klara $u -
- 700 1_
- $a Misik, Jan $u -
- 700 1_
- $a Novotny, Ladislav $u -
- 700 1_
- $a Ondracek, Karel $u -
- 700 1_
- $a Osickova, Jitka $u -
- 700 1_
- $a Mlcakova, Veronika $u -
- 700 1_
- $a Pohanka, Miroslav $u -
- 700 1_
- $a Skochova, Hana $u -
- 700 1_
- $a Vitula, Frantisek $u -
- 700 1_
- $a Treml, Frantisek $u -
- 773 0_
- $w MED00168352 $t Neuro endocrinology letters $x 0172-780X $g Roč. 33 Suppl 3(2012), s. 161-5
- 856 41
- $u https://pubmed.ncbi.nlm.nih.gov/23353861 $y Pubmed
- 910 __
- $a ABA008 $b sig $c sign $y a $z 0
- 990 __
- $a 20130703 $b ABA008
- 991 __
- $a 20131002123233 $b ABA008
- 999 __
- $a ok $b bmc $g 987666 $s 822366
- BAS __
- $a 3
- BAS __
- $a PreBMC
- BMC __
- $a 2012 $b 33 Suppl 3 $d 161-5 $i 0172-780X $m Neuro-endocrinology letters $n Neuro-endocrinol. lett. $x MED00168352
- LZP __
- $a Pubmed-20130703