Results 11 to 20 of about 4,105 (286)

Hepatotoxin-induced changes in the adult murine liver promote MYC-induced tumorigenesis. [PDF]

open access: yesPLoS ONE, 2008
Overexpression of the human c-MYC (MYC) oncogene is one of the most frequently implicated events in the pathogenesis of hepatocellular carcinoma (HCC).
Shelly Beer   +5 more
doaj   +2 more sources

Proteomic identification of IPSE/alpha-1 as a major hepatotoxin secreted by Schistosoma mansoni eggs. [PDF]

open access: yesPLoS Neglected Tropical Diseases, 2011
Eggs deposited in the liver of the mammalian host by the blood fluke parasite, Schistosoma mansoni, normally drive a T-helper-2 (Th2)-mediated granulomatous response in immune-competent mice.
Maha-Hamadien Abdulla   +3 more
doaj   +2 more sources

Iron as a Hepatotoxin

open access: yesDigestive Diseases, 2008
Although essential for life, iron in excessive amounts may be toxic. The liver is particularly subject to the toxic effects of iron, since it is the major site of iron storage. Several inherited and acquired human disorders may result in hepatic iron overload, the most common of which are genetic hemochromatosis (GH) and transfusional iron overload. GH
STAL, P
openaire   +3 more sources

1,1-Dichloroethylene: An Apoptotic Hepatotoxin? [PDF]

open access: yesEnvironmental Health Perspectives, 1984
Within 2 hr after 1,1-dichloroethylene administration, the following phenomena occur in livers of fasted rats: dilation and disruption of bile canaliculi, plasma membrane invagination and loss of microvilli, cytoplasmic vacuolation, and loss of density in mitochondrial matrices.
E S, Reynolds   +3 more
openaire   +4 more sources

Climate change and regulation of hepatotoxin production in Cyanobacteria [PDF]

open access: yesFEMS Microbiology Ecology, 2014
Harmful, bloom-forming cyanobacteria (CyanoHABs) are occurring with increasing regularity in freshwater and marine ecosystems. The most commonly occurring cyanobacterial toxins are the hepatotoxic microcystin and nodularin. These cyclic hepta- and pentapeptides are synthesised nonribosomally by the gene products of the toxin gene clusters mcy and nda ...
Michelle M, Gehringer, Nicola, Wannicke
openaire   +3 more sources

Molecular detection of hepatotoxic cyanobacteria in inland water bodies of the Marmara Region, Turkey [PDF]

open access: yesAdvances in Oceanography and Limnology, 2017
Blooms of cyanobacteria are an increasingly frequent phenomenon in freshwater ecosystems worldwide as a result of eutrophication. Many species can produce hepatotoxins that cause severe health hazards to humans.
Latife Köker   +3 more
doaj   +2 more sources

Experimental models used for the study of antihepatotoxic agents [PDF]

open access: yesJournal of Acute Disease, 2012
Both in vitro and in vivo liver models have been developed in the past years to study the hepatoprotective agents. These systems measure the ability of the test drug to prevent or cure liver toxicity (induced by various hepatotoxins) in experimental ...
Feroz Ahmad, Nahida Tabassum
doaj   +2 more sources

Ammonia as a neuro- and hepatotoxin: clinical aspects

open access: yesМедицинский совет, 2015
Ammonia is the most studied and, apparently, the most critical pathogenetic factor for hepatic encephalopathy (HE). The pathogenesis of PE is varied depending on the type of liver damage. Apart from neurotoxic properties, ammonia has general cytotoxic as
A. O. Bueverov
doaj   +2 more sources

Papaverine Revisited as a Hepatotoxin

open access: yesNew England Journal of Medicine, 1969
The proliferation of therapeutic agents during the past quarter-century has been accompanied by an increased frequency of drug-induced hepatic disease.1 , 2 Usually, the ability of an agent to produce hepatic injury is recognized within a few years of its introduction into clinical use.
Hyman J. Zimmerman
openaire   +3 more sources

Degradation of the cyanobacterial hepatotoxin microcystin by aquatic bacteria

open access: yesNatural Toxins, 1994
AbstractBacterial degradation of the cyanobacterial cyclic peptide hepatotoxin microcystin was confirmed in natural waters and by isolated laboratory strains. Degradation of 1 mg L−1 microcystin LR typically began 2‐8 days after addition to surface water samples. At concentrations greater than 1 mg L1 there was an initial slow removal of microcystin LR,
Jones, Gary J.   +3 more
openaire   +6 more sources

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