Biomedical subjects

J Lindén

Publications and source records attributed to J Lindén.

11 recordsLinked to original sources

PubMed1998

Isolation of an iridovirus from pike-perch Stizostedion lucioperca.

We have isolated a large virus from pike-perch Stizostedion lucioperca fingerlings with no signs of disease. The biochemical structural, and serological properties of this newly isolated virus suggest that it belongs to the family Iridoviridae. The virus multiplied and was cytopathogenic in several cultured fish cell lines. The virus has a DNA-containing genome and is assembled in the cytoplasm. When viewed in electron micrographs, the assembly sites showed a paracrystalline array of hexagonal nucleocapsids. The ultrastructure of the pike-perch virus resembled that of previously isolated fish iridoviruses. It is an enveloped icosahedral DNA virus. The diameter of the nucleocapsid in thin sections was 127 +/- 3 nm; in negatively stained preparates the size of the enveloped virus varied from 147 to 187 nm. In immunofluorescence the virus was stained by rabbit antisera against EHN (epizootic haematopoietic necrosis) virus, sheatfish iridovirus and cod iridovirus. The pathogenicity of the virus isolate was studied by inoculation into juvenile rainbow trout Oncorhyncus mykiss. Experimental infection under aquarium conditions suggested that the virus is apothogenic to rainbow trout. The infective virus could be recovered from the viscera of inoculated fish during the first week post-infection, after which the proportion of virus-positive fish declined over time. A small proportion of the fish still carried the virus 24 d post-inoculation.

Animals↗

PubMed1996

Mechanism by which 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) reduces circulating melatonin levels in the rat.

We have previously shown that the prototype for halogenated aromatic hydrocarbons, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), diminishes serum melatonin concentration at the same dose in both the most TCDD-susceptible (Long-Evans, Turku AB; L-E) and the most TCDD-resistant (Han/Wistar, Kuopio; H/W) rat strain. The change developed within 24 h and persisted for at least 28 days after TCDD exposure; was independent of the time of day and was not associated with any morphological damage to the pineal gland. In the present study, we investigated the mechanism of this endocrine effect. Despite a 40-50% decrease in circulating melatonin levels, the pineal content of melatonin, serotonin and 5-hydroxyindole acetic acid remained unaltered and the rate-limiting enzyme of pineal melatonin biosynthesis, N-acetyltransferase, displayed only a relatively minor suppression in activity (30%) in TCDD-treated L-E rats. Likewise, TSDD did not influence the ability of pineal glands from L-E rats to synthesize and secrete melatonin in ex vivo or in vitro experiments. TCDD accelerated the disappearance of exogenous melatonin from the serum in both rat strains. This enhancement probably did not originate in the liver, because liver perfusion studies revealed that even control rat livers were capable of total melatonin clearance in spite of the fact that the melatonin concentration far exceeded physiological levels. Urine excretion of the normal main metabolite of melatonin, 6-hydroxymelatoninsulfate, was reduced by TCDD treatment in both strains. This was accompanied by an altered HPLC pattern of metabolites, especially in H/W rats. We conclude that TCDD decreases serum melatonin levels in rats by enhancing the peripheral, evidently extrahepatic, metabolism of the hormone.

Animals↗

PubMed1995

Toxic equivalency factors do not predict the acute toxicities of dioxins in rats.

Risk evaluation of complex environmental mixtures of polychlorinated dibenzo-p-dioxins and related halogenated aromatic hydrocarbons (polychlorinated dibenzofurans, azo- and azoxybenzenes, naphthalenes and some of the biphenyls) is currently carried out by measuring the concentration of each congener in the mixture and then multiplying every figure by its specific constant, toxic equivalency factor (TEF). All congeners are thought to produce highly similar effects albeit at different doses, and the TEFs are believed to represent the potencies of the congeners relative to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), considered the most toxic derivative of this class of environmental contaminants. Here we compared the acute toxicities of TCDD, 1,2,3,7,8-penta-, 1,2,3,4,7,8-hexa- and 1,2,3,4,6,7,8-heptachloro-dibenzo-p-dioxin in the most TCDD-susceptible (Long-Evans Turku AB; L-E) and the most TCDD-resistant (Han/Wistar kuopio; H/W) rat strain. While L-E rats exhibited the expected rank order of sensitivities to the four dioxins, the higher chlorinated dioxins were more toxic than TCDD (in terms of acute lethality) to H/W rats, with the hexachlorodioxin showing the greatest potency. Even if the doses were adjusted according to the LD50 values, both biochemical and morphological effects elicited by the dioxins turned out to depend, often critically, on strain, congener or the interaction of these two determinants. These findings demonstrate that the dioxins have distinct profiles of acute toxicities and underscore the importance of response and test organism in defining the TEFs.

Animals↗

PubMed1995