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At least 19 recordsLinked to original sources

Inhibition of neutrophil chemotaxis by organotin compounds.

Organotin compounds such as Bu2SnCl2, Bu3SnCl and Ph3SnCl suppressed significantly not only chemotactic response of neutrophils to stimulation by the chemoattractant fMet-Leu-Phe but also phospholipase activity in situ as measured by the release of [1-14C] arachidonic acid previously incorporated into phospholipids. Moreover, these suppressions were dose dependent and a parallelism was found between dose-dependent inhibition of chemotaxis and that of arachidonate release. These results suggest that the chemotactic response is controlled by the activation of phospholipase activity in neutrophils, and that the inhibitory effects of these organotin compounds on chemotactic response reflect the blockage of phospholipase activation system regulated by phosphorylation of lipomodulin.

Animals↗

[Studies on the antitumor activity of organotin compounds].

Organotin compounds were found to obviously inhibit the activity of phospholipid/Ca(2+)-dependent protein kinase (PKC) in rat brain tissue and the proliferation of tumor cell lines in vitro. The results showed that a correlation exists between the effects on PKC and anti-proliferative and antitumor activities. The structure-activity relationship was shown to be as follows: (1) R, the organic group determines the biological activity; (2) electronegativity of the halogen can affect the activity. The organotin compounds inhibit tumor cells by its [SnR2]2+, and inhibit G1-->S phases of HL-60 cell cycle. The IC50 of [SnPh2F2], [SnPh2(CysOS)].H2O and [SnPh2Cl2.phen(CH3)2] are respectively 25, 15 and 20 mumol.L-1 on PKC, 0.5, 4.0 and 0.3 mumol.L-1 on HL-60 cells, 2.7, 9 and 1.5 mumol.L-1 on BEL-7402 cells, 2.2, 15 and 5.0 mumol.L-1 on KB cells. But no induction of differentiation of leukemic cell lines HL-60 and K562 was observed.

Animals↗

Ecotoxicology of organotin compounds.

Organotin compounds are ubiquitous contaminants in the environment. The high biological activity of some compounds toward aquatic organisms lead to deleterious impacts in aquatic ecosystems. Here, the aquatic ecotoxicology of organotins is reviewed based on a multidisciplinary approach involving environmental chemical, toxicological, and ecological aspects. Basic results were obtained both with field and laboratory studies, and some of the most important recent results and conclusions are critically reviewed. The contamination of and fate in aquatic systems is reported and linked with effects at different levels of biological organization. Major emphasis is placed on the development of a concept of ecotoxicology that encompasses not only effect assessment alone, but also integrates environmental chemistry with aquatic toxicology. Thereby, the influence of speciation for bioavailability, basic modes of toxic action, and aquatic toxicity are discussed. This case study on organotins allows to a certain extent generalizations to ecotoxicology in general.

Animals↗

[Suppression of Penicillium purpurogenum growth by organotin compounds].

We studied the effect of organotin compounds and their mixtures with N-cetylpyridinium chloride on the accumulation of biomass by Penicillium purpurogenum. Ditributylstannylic ester of fumaric acid at a concentration of 0.005 micrograms/ml was shown to inhibit the accumulation of biomass. If an organotin compound was used in combination with N-cetylpyridinium chloride, the fungicide effect was greater at a lower dose of the organotin compound in the mixture. Organotin compounds and their mixtures with N-cetylpyridinium chloride suppress protein biosynthesis in the fungal mycelium, increasing protein content in the cultural broth. The mechanism of action of organotin compounds on the growth of P. purpurogenum is discussed.

Cetylpyridinium↗

Organotin compounds and their interactions with microorganisms.

Organotin compounds are ubiquitous in the environment. The general order of toxicity to microorganisms increases with the number and chain length of organic groups bonded to the tin atom. Tetraorganotins and inorganic tin have little toxicity. Because of their lipophilicity, organotins are regarded as membrane active. There is evidence that the site of action of organotins may be both at the cytoplasmic membrane and intracellular level. Consequently, it is not known whether cell surface adsorption or accumulation within the cell, or both is a prerequisite for toxicity. Biosorption studies on a fungus, cyanobacteria, and microalgae indicates that cell surface binding alone occurred in these organisms, while studies on the effects of TBT (tributyltin) on certain microbial enzymes indicated that in some bacteria TBT can interact with cytosolic enzymes. Microorganism-organotin interactions are influenced by environmental conditions. In aquatic systems, both pH and salinity can determine organotin speciation and therefore reactivity. These environmental factors may also alter selectivity for resistant microorganisms in polluted systems. Tin-resistant microorganisms have been identified, and resistance can be either plasmid or chromosomally mediated. In one TBT-resistant organism, an Altermonas sp., an efflux system was suggested as the resistance mechanism. Biotransformation of organotin compounds by debutylation or methylation has been observed. These reactions may influence the toxicity, mobility, and environmental fate of organotin compounds.

Bacteria↗

Prolonged induction of hepatic haem oxygenase and decreases in cytochrome P-450 content by organotin compounds.

The administration of organotin compounds to rats in single doses causes a significant and prolonged induction of haem oxygenase and a sustained decrease in haemoprotein content in the liver. The extent of induction of hepatic haem oxygenase varied between 3 and 5-fold at 72h after a single injection of water-insoluble organotins of differing structure. The alterations in haem metabolism produced by tricyclohexyltin hydroxide were studied in detail. The effects were dose-dependent, with doses as low as 3.75 mg/kg body wt. resulting in significant induction of haem oxygenase and a decrease in cytochrome P-450 and cytochrome b5 contents at 72h in the liver. The effects with time of a single dose of tricyclohexyltin on various parameters of liver haem metabolism were also examined. The organotin produced a substantial and very prolonged induction of haem oxygenase accompanied by a steady decline in cytochrome P-450 content for periods up to 8 days. The long duration of action of these organotins with respect to induction of haem oxygenase and depletion of cellular haemoprotein content provides a highly sensitive metabolic system with which to define further the toxic potential of organometals as well as to study the adaptive responses in liver to long-term perturbations of haem metabolism by foreign chemicals.

Animals↗

[Recent progress in the study of analytical methods, toxicity, metabolism and health effects of organotin compounds].

Over the years, a variety of uses has been found of organic tin compounds as fungicides, as stabilizers in plastics and for other industrial uses. The purpose of this article is to summarize and review the results so far obtained as to the analytical method for organotins in biological samples, the toxicity, metabolism, and biochemical and health effects of organotin compounds. 1) Many methods have been developed for analysis of organotin compounds by spectrophotometry, polarography, gas- or liquid-chromatography, etc. These methods, however, are mainly for analysis of organotins in standard solutions or in water, and are not suitable for organotin compounds in biological samples. Recently, we have developed several methods for analysis of various kinds of organotin compounds in biological samples. These methods are able simultaneously to separate and determine trace amounts (at nanogram order) of organotin compounds and their metabolites in the same biological samples. 2) Acute toxicity of organotin compounds which appeared on the literature are summarized. Trialkyl and triaryl compounds seem to be more toxic than the tetra-, di-, or mono-compounds of the same chain length. With an increase in the number of C atoms the toxicity of alkyl compounds decreases. Aryltin compounds are less toxic than alkyltin compounds. 3) Intestinal absorption sites for tetra-alkyltins are jejunum and duodenum, and those for trialkyltins are ileum and jejunum. A considerable amount of orally administered tetra- and trialkyltins of low molecular weights are absorbed, but only very little of the other organotin compounds seems to be absorbed from the gastrointestinal tract. Absorbed organotin compounds rapidly undergo dealkylation by the microsomal mono-oxygenase system dependent on cytochrome P-450 in the liver, brain or other organs, and the compounds and their metabolites distribute to the whole body, ultimately being excreted into urine, bile and faeces. The biological half life of organotin compounds in mammals is usually short, a half of the amount of tributyl- and triphenyl-tins deposited in the body disappearing in several days. A part of organotin compounds excreted into bile is demonstrated to have been absorbed from the intestine and to circulate in the body via enterohepatic circulation. 4) Specific effects of organotin compounds on the biological systems and health include disturbance of the structure and function of the central nervous system (interstitial edema of white matter), inhibited oxidative phosphorylation in mitochondria of cells, atrophy of the thymus and thymus dependent lymphoid tissues resulting in the dysfunction of T cells for immunity, inhibited enzyme activity, lesions in the liver and bile ducts etc., although some specificity is observed among species of animals and organotin compounds. Recently we found that a single oral administration of triphenyltin fluoride to rabbits induces transient diabetes and diabetic lipemia by inhibiting insulin secretion from morphologically normal pancreatic B-cells...

Animals↗

Studies on the mechanism of oxidative phosphorylation. ATP synthesis by submitochondrial particles inhibited at F0 by venturicidin and organotin compounds.

Oligomycin,N,N'-dicyclohexylcarbodiimide (DCCD), venturicidin, and tetracoordinate organotin compounds (R3SnX) are potent inhibitors of the mitochondrial ATP synthase complex, all acting on the membrane sector, F0. Oligomycin and DCCD inhibit proton translocation through F0 and energy transfer between F0 and the catalytic sector, F1, of the ATP synthase complex. Our results have shown that venturicidin and organotin compounds (tributyltin and triphenyltin chloride were used) greatly attenuate these processes, but do not cause complete inhibition. As a result, bovine submitochondrial particles (SMP) treated with venturicidin or tributyltin chloride were shown to be capable of ATP hydrolysis and synthesis, albeit at very slow rates. We had shown previously that in ATP synthesis Vmax and apparent Km for ADP and Pi increase or decrease, respectively, as the steady-state membrane potential is elevated or lowered (Matsuno-Yagi, A., and Hatefi, Y. (1986) J. Biol. Chem. 261, 14031-14038). These changes occurred at constant Vmax/Km, suggesting that the apparent Km changes were due mainly to kcat changes. Results presented here show that, in respiring SMP treated with venturicidin or organotin compounds, the membrane potential is near the static-head level, but the slow rate of ATP synthesis takes place with a low KmADP value of 2-3 microM. In agreement with our previous conclusions, these results indicate that it is not the membrane potential per se that affects KmADP during ATP synthesis, but rather it is the rate of energy transfer from F0 to F1 that influences both Vmax and KmADP. Further conclusions from the above studies have been discussed in relation to the possible mechanism of energy transfer between F0 and F1 and the manner in which venturicidin and organotin compounds might attenuate this process.

Adenosine Triphosphate↗

Distribution pattern of organotin compounds at different trophic levels of aquatic ecosystems.

Organotin compounds including methyl- and butyltin species were determined in selected aquatic specimens (fish muscles, fish liver, mussels, algae) as well as in sediment and water from the mud flats of the German North Sea and the River Elbe. The concentration of tributyltin (TBT) ranged between 27-202 ng/g (fresh mass) in fish muscles, 54-223 ng/g (fresh mass) in fish liver, 10-25 ng/g (fresh mass) in common mussels and 42-97 ng/g (fresh mass) in bladderwrack. The concentration of total organotin compounds (mono-, di-, and trimethyltin + mono-, di-, and tributyltin) in water samples along the River Elbe up to the Elbe estuary ranged between 30-96 ng/l. Retrospective investigation of butylin compounds in mussel samples from the North Sea was performed by the analysis of cryogenically stored samples from 1985. A comparison of the results with that in muscles from 1993 shows that the total tin content and the TBT content decreased from 1985-1993 by a factor of 3.5 and 6.5, respectively. In addition estimated bioconcentration factors (BCF) for organotin compounds in samples from different trophic levels are presented.

Animals↗

Inhibition of mouse spleen cell activity by organotin compounds: effect of attachment of a maltose residue to the organotin group.

Studies are reported on the inhibition of DNA synthesis and the lowering of cell viability caused by bis(tributyltin) oxide in mouse spleen cells cultured in the presence and absence of the B-lymphocyte mitogen, bacterial lipopolysaccharide. When a maltose residue is introduced into the organotin compound these toxic effects are increased. It is suggested that the maltose residue facilitates entry of the organotin compound into the cells.

Animals↗

Laser-excited atomic fluorescence in a flame as a high-sensitivity detector for organomanganese and organotin compounds following separation by high-performance liquid chromatography.

The coupling of a high-performance liquid chromatograph with a sensitive and selective laser-excited atomic fluorescence spectrometry (LEAFS) detector is described. In connection with this, a study of the signal and noise characteristics of instrumentation for dispersive, nondispersive, and front surface LEAFS is reported together with a comparison of the sensitivity and selectivity achieved with high-performance liquid chromatography (HPLC)-flame LEAFS, HPLC-ultraviolet (UV), and HPLC-continuum source excited flame atomic fluorescence spectrometry (AFC) instrumentation. The HPLC-flame LEAFS instrumentation was applied to an investigation of the Mn species responsible for (methylcyclopentadienyl)manganese tricarbonyl (MMT) toxicity in rats. The detection limits for various organomanganese species by HPLC-flame LEAFS ranged from 8 to 22 pg of manganese. Recovery of these compounds from rat urine varied between 80% and 100%, with a reproducibility of between 4% and 8% relative standard deviation. Preliminary data for the HPLC-flame LEAFS determination of toxic alkyltin compounds are reported.

Chromatography, High Pressure Liquid↗

Inhibition of the enzymatic activity of ligandin by organogermanium, organolead or organotin compounds and the biliary excretion of sulfobromophthalein by the rat.

Ligandin binds several classes of compounds, has glutathione-S-transferase activity and is postulated to function in the intracellular transport of substances which bind to it and/or are substrates for its enzymatic activity. The effects of a group of organometals reported to inhibit the enzymatic activity of ligandin on the biliary excretion of sulfobromophthalein have been investigated to determine what role the enzymatic activity of ligandin has with respect to the biliary excretion of the dye. Triethyllead reduced the rate of dye excretion into the bile without affecting blood pressure, blood or liver sulfhydryl compounds or the volume of bile flow. The organometal had no effect on the initial rate of plasma dye clearance. Inhibited biliary sulfobromophthalein excretion by triethylead-treated rats correlated with relative increases in liver and bile unconjugated dye, decreases in liver and bile conjugated dye and reduced glutathione-S-aryltransferase activity in supernatant fractions isolated from the liver. The results clearly demonstrated that the tested organometals can inhibit the enzymatic activity of ligandin in vivo and suggested that, if ligandin has a role in the translocation of the dye from the blood to the liver, the enzymatic activity of the protein may not be involved.

Animals↗

Acute and sublethal effects of organotin compounds on aquatic biota: an interpretative literature evaluation.

The objectives of this review were to: (1) collect, synthesize, and interpret acute and sublethal organotin toxicity data in both freshwater and estuarine-marine ecosystems; (2) present environmental water column and sediment concentrations of organotin compounds in both freshwater and estuarine-marine systems to facilitate interpretation of toxicity data; and (3) identify deficiencies in available data to recommend areas of future research for assessing ecological effects of organotin compounds in aquatic systems. The following recommendations are suggested: (1) evaluation of the bioavailability of organotin compounds in aquatic systems; (2) assessment of the relationship between physicochemical characteristics of organotin compounds and subsequent toxicity effects on aquatic organisms; (3) determination of organotin effects on food chains; (4) evaluation of the specific mechanisms and modes of toxicity for organotin compounds with aquatic biotia; (5) evaluations of the adaptive responses of aquatic biota to organotins; (6) measurement of organotin concentrations in testing chambers throughout toxicity tests using peer-reviewed analytical techniques (nominal concentrations can provide misleading data); (7) assessment of long-term "low level" exposures of organotin compounds on histological, histochemical, behavioral, and physiological responses of aquatic biota; and (8) toxicity assessment of plasticizer organotin compounds to aquatic biota.

Amphibians↗

Electrostatic inhibition of hemolysis induced by organotin compounds.

The effect of cations on the kinetics of hemolysis caused by organotin compounds was studied. The ions used in the investigation diminish or totally inhibit hemolysis of red cells induced by organotin compounds. The degree of inhibition depends both on the kind of ion and the compounds that induce hemolysis. The ions Zn2+, Co2+, and Cd2+ present in the medium at 50 microM concentration totally protect the erythrocytes against hemolysis induced by the compound (C3H7)3SnCl. The study has also shown the monovalent ions K+ and trimethyldodecylammonium bromide are less potent inhibitors of hemolysis than divalent ions, which is not the case for two non-ionic organotin compounds only. The studies performed indicate that hemolysis induced by organotin compounds is inhibited due to electrostatic interaction between the cations selected and erythrocyte membrane.

Animals↗

Comparative studies on the induction of muscle contracture in mouse diaphragm and Ca2+ release from sarcoplasmic reticulum vesicles by organotin compounds.

Effects of organotins, including triethyltin and tributyltin, on skeletal muscle were studied with diaphragm and isolated sarcoplasmic reticulum membrane vesicles. Triethyltin induced muscle contracture in mouse diaphragm while tributyltin had comparatively less potency and efficacy in inducing the muscle contracture. The contracture induced by tributyltin was inhibited when the diaphragm was pretreated with low Ca2+ medium or caffeine while the contracture induced by triethyltin persisted in the Ca2+-free medium but was inhibited by pretreatment of caffeine. Pretreatment of dithiothreitol blocked the contracture induced by tributyltin but not that by triethyltin. Triethyltin dose-dependently induced Ca2+ release from sarcoplasmic reticulum vesicles and inhibited the Ca2+-ATPase activity. These results suggested that triethyltin induced contracture in mouse diaphragm was mainly by induction of Ca2+ release and inhibition of Ca2+ uptake of the internal Ca2+ storage site the sarcoplasmic reticulum, while the tributyltin induced contracture might be due to enhancement of extracellular Ca2+ influx which further induce the release of internal Ca2+ through the Ca2+-induced Ca2+ release mechanism.

Animals↗

Chemical species of organotin compounds in sediment at a marina.

A bottom sediment collected in a marina was analyzed for organotin species, and >20 organotin compounds including biodegraded ones were confirmed by comparison with the synthesized standards using gas chromatography (GC)/mass spectrometry and a GC/atomic emission detection system. Their structures were also determined in comparison with those in a technical grade of tri-n-butyltin chloride (TBTC). Eleven organotin compounds were found in the technical TBTC. Among them, unexpected organotin compounds, such as di-n-butyl(2-ethylhexyl)tin chloride and di-n-butyloctyltin chloride, were identified, although the levels were low. These compounds were also found in the sediment sample. The relationship between organotin compounds in the technical TBTC and those in marine products was also discussed.

Chromatography, Gas↗

Differential effects of organotin compounds on voltage-gated potassium currents in lymphocytes and neuroblastoma cells.

Effects of organotin compounds were studied on voltage-gated K+ current in whole-cell voltage clamped lymphocytes and in N1E-115 neuroblastoma cells. In human peripheral blood lymphocytes the immunotoxic compounds dibutyltinchloride (DBT, 2.5 microM) and triphenyltinchloride (TPhT, 2.5 microM) decrease the peak amplitude of the K+ current and prolong time to peak. Tributyltinchloride (TBT, 2.5 microM) decreases the K+ current to a greater extent than DBT and TPhT, without affecting the time to peak. The neurotoxic organotin compound trimethyltinchloride (TMT, 2.5 microM) does not affect the voltage-gated K+ current in lymphocytes. Similar effects of DBT were observed in freshly isolated and PHA-activated human lymphocytes and with rat thymocytes. On the other hand, in mouse N1E-115 neuroblastoma cells, none of the organotin compounds altered the voltage-dependent K+ current. In human lymphocytes DBT affects both the peak amplitude and the time to peak of the K+ current in a concentration-dependent manner. At the maximum concentration of 10 microM tested, the peak amplitude of the K+ current was reduced to 22 +/- 4% of the control current. The IC50 and slope factor for block of the peak outward current by DBT amounts to 6.7 +/- 0.4 microM, and 2.7 +/- 0.4, respectively. The delay in K+ current activation does not saturate. At 10 microM DMT increases the time to peak to 332 +/- 12% of the control value. The present results suggest that the effects by DBT originate from two separate interactions with the voltage-gated K+ channel at the extracellular site of the membrane: a direct effect on the closed K+ channel causing a delay in current activation and a membrane-related effect causing inhibition of the K+ current. The differential effects of the organotin compounds may relate to their differential toxicological action.

Animals↗