Gene/Protein Disease Symptom Drug Enzyme Compound
Pivot Concepts:   Target Concepts:
Query: EC:1.3.5.1 (succinate dehydrogenase)
 8,177 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

In order to investigate the potential ecotoxicity of diethanolamine (DEA), a battery of model systems was developed. DEA is widely used as a chemical intermediate and as a surface-active agent in cosmetic formulations, pharmaceuticals and agricultural products. DEA was studied using ecotoxicological model systems, representing four trophic levels, with several bioindicators evaluated at different exposure time periods. The battery included bioluminescence inhibition of the bacterium Vibrio fischeri, growth inhibition of the alga Chlorella vulgaris and immobilization of the cladoceran Daphnia magna. Cell morphology, total protein content, neutral red uptake, MTS metabolization, lysosomal function, succinate dehydrogenase activity, G6PDH activity, metallothionein levels and EROD activity were studied in the hepatoma fish cell line PLHC-1, derived from Poeciliopsis lucida. The systems most sensitive to DEA were both D. magna and V. fischeri, followed by C. vulgaris and the fish cell line PLHC-1. The most prominent morphological effect observed in PLHC-1 cultures exposed to DEA was the induction of a marked steatosis, followed by death at high concentrations, in some cases by apoptosis. The main biochemical modification was a nearly three-fold increase in metallothionein levels, followed by the stimulations of lysosomal function and succinate dehydrogenase and G6PDH activities. Judging by the EC(50) values in the assay systems, DEA is not expected to produce acute toxic effects in the aquatic biota. However, chronic and synergistic effects with other chemicals cannot be excluded.
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PMID:Ecotoxicological evaluation of diethanolamine using a battery of microbiotests. 1609 69

There is limited information available about the potential environmental effects of chloroquine (CQ), a widely used antimalarial agent and a promising inexpensive drug in the management of HIV disease. The acute effects of CQ were studied using four ecotoxicological model systems. The most sensitive bioindicator was the immobilization of the cladoceran Daphnia magna, with an EC50 of 12 microM CQ at 72 h and a non-observed adverse effect level of 2.5 microM CQ, followed very closely by the decrease of the uptake of neutral red and the reduction of the lysosomal function in the fish cell line PLHC-1 derived from the top minnow Poeciliopsis lucida, probably due to the selective accumulation of the drug into the lysosomes. There was significant cellular stress as indicated by the increases on metallothionein and glucose-6P dehydrogenase levels after 24 h of exposure and succinate dehydrogenase activity mainly after 48 h. No changes were observed for ethoxyresorufin-O-deethylase (EROD) activity. The least sensitive model was the inhibition of bioluminescence in the bacterium Vibrio fischeri. An increase of more than five-fold in the toxicity from 24 to 72 h of exposure was observed for the inhibition of the growth in the alga Chlorella vulgaris and the content of total protein and MTS tetrazolium salt metabolization in PLHC-1 cells. At the morphological level, the most evident alterations in PLHC-1 cultures were hydropic degeneration from 25 microM CQ after 24h of exposure and the presence of many cells with pyknotic nuclei, condensed cytoplasm and apoptosis with concentrations higher than 50 microM CQ after 48 h of exposure. In conclusion, CQ should be classified as harmful to aquatic organisms.
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PMID:Ecotoxicological evaluation of the antimalarial drug chloroquine. 1615 18

Bromobenzene (BrB) is used as a solvent for crystallization and as an additive to motor oils and may be released into the environment through various waste streams. However, there is limited available information about the toxic hazard of BrB in the aquatic environment. Consequently, the ecotoxicological effects induced by BrB were investigated using five model systems with representants from four trophic levels. The battery included bioluminescence inhibition of the bacterium Vibrio fischeri, growth inhibition of the alga Chlorella vulgaris and immobilization of the cladoceran Daphnia magna. Total protein content, neutral red uptake and MTS metabolization were reduced, while lysosomal function, succinate dehydrogenase activity, G6PDH activity and leakage, metallothionein levels and EROD activity were stimulated in PLHC-1 and RTG-2 fish cell lines. The most sensitive bioindicator was the bioluminiscence of V. fischeri, with an EC(50) of 0.04mM BrB at 15min and a non-observed adverse effect level of 0.02 mM BrB. There is a large difference in sensitivity to BrB among the model systems probably due to the metabolic capacity of the different species. PLHC-1 cells were more sensitive to BrB than RTG-2 cells. The most prominent morphological effects observed were hydropic degeneration, loss of cells and of the perinuclear pattern of distribution of lysosomes. Therefore, BrB should be classified as toxic to aquatic organisms.
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PMID:Ecotoxicological assessment of bromobenzene using a test battery with five model systems. 1712 77