Inactivation of bacteriophage T4 by organic and inorganic tin compounds

Summary Butyltins and inorganic tins inactivated bacteriophage T4. The effect was on the phage and not on its host,Escherichia coli. The order of effectiveness was SnCl₄monobutyltin>dibutyltin>tributyltinSnCl₂. For the butyltins and SnCl₄ this was the reverse of the order of effectiveness usually observed for plants, animals, and microorganisms. This pattern suggests that degradation of tributyltin does not always detoxify it. Monobutyltin (MBT), the most effective organotin, was more effective at pH 4 than at higher pH values and it was more eeffective at low strength. Inactivation proceeded more rapidly at 37°C than at 18°C. The results of experiments in which the ratio of phage to MBT was varied suggests that tin compounds may act by flocculating phage particles. Zinc, which is bound by phage short tail fibers (P12), inhibited phage inactivation by MBT, suggesting that MBT may act upon these tail fibers.     

Sex alteration in soft-shell clams (Mya arenaria) in an intertidal zone of the Saint Lawrence river (Quebec,Canada)

The purpose of this study was to verify whether any changes in sex ratio might occur in soft-shell clams (Mya arenaria) located in an intertidal harbor zone located at the mouth of the Saguenay Fjord in the Saint Lawrence estuary (Baie Sainte-Catherine (BSC), Québec, Canada) likely to be contaminated by organotin compounds. Bivalves were harvested at the BSC harbor site and from two reference sites. Condition index (weight to length ratio), gonado-somatic index, sex ratio, vitellin-like proteins, organotin concentrations in gonad tissue, maturation stages of the gonads, the number of estradiol-17beta binding sites and the capacity of female gonad extracts to produce estradiol-17beta were determined in collected animals. Results showed that sex ratio in clams was significantly skewed toward males. Moreover, the condition and gonad-somatic indices, vitellin-like proteins in female gonads and the capacity of female gonads to produce estradiol-17beta were significantly reduced at the harbor site with respect to the reference sites. Maturation status of male gonads was clearly delayed at the harbor site. Additionally, gonad tissue contained tributyltin (TBT) at an average level of 109+/-18 ngSn/gdry wt. at the harbor site while organotins were not detected from the reference sites. Finally, female gonads had a higher number of unoccupied estradiol binding sites at the harbor site indicating low levels of this steroid in this tissue. Overall, this paper is first to report that clams collected in the vicinity of a TBT contaminated harbor are subject to masculinizing effects which seems to be consistent with biological effects that organotins are known to exert toward some other marine invertebrates.     

三种前鳃亚纲海产腹足类性畸变现象的组织学研究

有机锡污染可以导致海产腹足类雌性个体产生性畸变现象。本文报道了阿文绶贝(Mauritia arabica)、褐棘螺(Chicoreus brunneus)和桶形芋螺(Conus betulinus)三种前鳃亚纲腹足类正常雄性个体和性畸变个体雄性生殖器官的组织学结构。结果表明,不同种间雄性个体的输精管和阴茎的结构存在开放和封闭两种类型,封闭型是由开放型进化而来。虽然性畸变个体的雄性生殖器官与正常雄性个体的在组织结构上无明显差异,但性畸变个体的雄性生殖器官并不完整,无法行使生殖功能。由于内分泌扰乱物质对人和动物影响的相似性,使得海产腹足类性畸变现象应受到人们的重视。     

Effects of organotin and organolead compounds on yeasts

Summary Four methods were used to screen nine organotin and two organolead compounds for toxicity to 29 yeasts, representing 10 genera. Center well diffusion plates were useful in comparing the sensitivity of yeasts to the most toxic organometals but were not useful for comparisons between compounds because of differences in diffusion rates and lack of sensitivity. Two-layer diffusion plates (density gradient plates) were also of limited use for comparisons between compounds but provided quantitative information on toxicity and allowed comparisons between organisms. Two-dimensional diffusion plates were useful for estimating the effect of pH on organometal toxicity. Release of K⁺ from cell suspensions measured using a K⁺-electrode provided quantitative information and allowed comparisons between compounds and organisms. The presence of 3% NaCl in cell suspensions decreased the rates and extent of organotin-induced K⁺ release. Yeasts varied in their sensitivity from strain to strain, but tributyltin was the most toxic compound tested. Mono- and dimethyltins were the least toxic. Triphenyltin, dibutyltin, monobutyltin, trimethyltin, triethyltin, diethyllead, diethyltin, and dimethylleads showed intermediate toxicity, but triphenyltin and monobutyltin were the most toxic among the group.     

Toxicity of organotins towards cyanobacterial photosynthesis and nitrogen fixation

Abstract Inhibition of photosynthesis by a range of organotin compounds in Plectonema boryanum was concentration-dependent and decreased in the order tributyltin (Bu₃SnCl) > tripropyltin (Pr₃SnCl) ≥ dibutyltin (Bu₂SnCl₂) ≥ triphenyltin (Ph₃SnCl) > triethyltin (Et₃SnCl) > trimethyltin (Me₃SnCl) > monobutyltin (BuSnCl₃). IC₅₀ values were determined for the most toxic organotin species and varied from approximately 1.2 μM for Bu₃SnCl to approximately 13 μM for Ph₃SnCl. A similar order of inhibition of photosynthesis was observed in Anabaena cylindrica , although here IC₅₀ values were slightly lower (e.g. approximately 1 μM for Bu₃SnCl and 5 μM for Ph₃SnCl).Nitrogenase activity was generally more sensitive to inhibition by organotin compounds than photosynthesis in A. cylindrica and this was particularlyy evident for Bu₂SnCl₂; approximate IC₅₀ values for Bu₂SnCl₂ were 3 and 9 μM, as estimated by nitrogenase activity and photosynthesis, respectively. These results indicate that organotin compounds have the potential to inhibit cyanobacterial metabolism in aquatic systems.     

Effects of Organotins on Rat Brain Astrocytes in Culture

Abstract: The interaction of triethyltin (TET) and trimethyltin (TMT) with rat brain astrocytes in vitro was investigated. Both compounds are highly neurotoxic after in vivo application, cause neurobehavioral changes, and elicit neuronal and glial responses in the CNS. In this study, 5-week-old cultures were exposed to TMT or TET (0.1–2.5 µM) for 24 h. A concentration-dependent cytotoxicity was observed for both agents by vital dye uptake assay using neutral red (NR). The order of potency for half-maximal cytotoxicity (NR-50) was TET (0.7 µM)> TMT (2.5 µM), in agreement with results found after in vivo administration. TET and TMT caused similar morphological changes: large holes extending through the plasma membrane appeared initially in the flattened cell bodies, cytoplasmic extensions were retracted, and long cellular processes formed. Later, the cell bodies rounded up and had only a few extremely long and thin processes. Indirect immunofluorescence staining using anti-vimentin and anti-glial fibrillary acidic protein (GFAP) antibodies revealed that the orderly array of the intermediate filament system was severely disturbed. At lower concentrations, an increased bundling was observed, and at higher concentrations the disassembly of the intracellular framework was seen, and cellular staining appeared rather diffuse. Western blot analysis of cellular extracts was carried out to determine the protein levels of GFAP and vimentin. In this culture system, TET and TMT caused an almost two-fold increase in the levels of GFAP at concentrations around and below NR-50, indicating that astrocytes react to organotics independently of neuronal signals. Concomitantly, TET (0.7 µM) and TMT (2.5 µM) led to a 63% decrease in the activity of ecto-5′-nucleotidase, which in addition to its enzymatic function, represents a transmembrane cell surface protein and has been implicated in cellular adhesion and cell communication processes. Thus, triorganotins directly affect astrocytes in culture and alter their functional stage even in the absence of neurons.     

Triphenyltin inhibits photosynthesis and respiration in marine microalgae

Summary The effects of diphenyltin and triphenyltin (TPhT) on gross photosynthesis and respiration by the diatomSkeletonema costatum (Greville) Cleve and the chlorophyteDunaliella tertiolecta (Butscher) were investigated by measuring the rates of change of oxygen concentration in samples which were alternately illuminated unilluminated. Measurements were carried out for 90 min after organotin addition. Triphyltin at concentrations in the nM to M range inhibited photosynthesis and respiration in both ogranisms. Levels of TPhT inhibiting these processes were two to three orders of magnitude higher forD. tertiolecta than forS. costatum. Photosynthesis and respiration byD. tertiolecta were resistant to diphenyltin at concentrations up to its limit of solubility (0.84 mM). WithS. costatum, inhibitory levels of diphenyltin were one to two orders of magnitude higher than those for triphenyltin. Inhibition was often progressive over the period after organotin addition. This effect varied in intensity and was more noticeale with the more resistantD. tertiolecta. Comparison of our results with levels of organotins which have been obeserved by others in Mediterranean coastal waters indicate that environmental levels of TPhT could influence phytoplankton composition and dynamics.     

Toxic effects of tin compounds on microorganisms

Summary Organotins are used for industrial and agricultural purposes and in antibiologic agents. They are significantly more toxic than inorganic tins, and eventually reach the environment where they can be toxic to a wide variety of organisms. Particular attention has been given to tributyltins which are highly toxic components of antifouling paints. Realization that the molecular species of organotin influences fate and effects of organotins led to development of sensitive methods for quantifying individual molecular species. Even though such methods are now available, little information has been obtained on the ability of microorganisms to bioaccumulate tin compounds. Trisubstituted alkyl and aryltins (R₃Sn's) are more toxic than disubstituted compounds (R₂Sn's) while monosubstituted organotins (RSn's) are still less toxic. R₄Sn's are toxic only if they are metabolized to R₃Sn's. Among trisubstituted compounds propyl-, butyl-, pentyl-, phenyl-, and cyclohexyl Sn's are generally the most toxic to microorganisms. Toxicity in the R₃Sn series is related to total molecular surface area of the tin compound and to the octanol:water partition coefficient,K _ow, which is a measure of hydrophobicity; a highK _ow indicates greater hydrophobicity and predicts greater toxicity. Care must be taken when testing the toxicity of tin compounds, for a number of biological, physical and chemical factors can influence the apparent toxicity. Although little is known of the effects of tin compounds on microbial processes, a number of bacterial processes can be inhibited by organotins and all relate to membrane functions. They include effects on energy transduction, solute transport and retention and oxidation of substrates. Very little is known of how organotins exert their toxic effects on algae and fungi; Information on effects on chloroplasts and mitochondria stems principally from animal systems and from higher plants. Triorganotins act against chloroplasts and mitochondria by causing swelling, by acting as ionophores and by acting against ATPase, while diorganotins appear to act by binding to dithiol groups on enzymes and cofactors. Nucleic acids do not seem to be affected at environmentally relevant concentrations. Virtually nothing is known of the action of tin compounds on microbial enzymes, but resistant mutants are easy to obtain and should facilitate work to understand modes of microbial interaction with tin compounds and mechanisms of resistance.