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.     

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.     

Effects of butyltins and inorganic tin on chemotaxis of aquatic bacteria

Summary Tributyltin (TBT) and its degradation products dibutyltin (DBT), monobutyltin (MBT) and Sn^IV were toxic toPseudomonas fluorescens SHC-6 andSerratia sp. Gil-1 with EC₅₀ values in the range of 10^–3 to 10^–4M. These four compounds were negative chemotactic agents forP. fluorescens, and the butyltins were negatively chemotactic forSerratia sp. at concentrations over four orders of magnitude lower than the EC₅₀ values.l-Aspartate was a positive chemotactic agent for both organisms. TBT, DBT and MBT negated the effect ofl-aspartate onP. fluorescens but not onSerratia sp. Thus, TBT has the potential to affect microbial populations at concentrations much lower than those which prevent growth, and degradation of TBT does not always detoxify it. SnCl₄ was less toxic than TBT or DBT to these organisms and it was not chemotactic forSerratia sp. Gil-1. Tributylamine and tributylphosphate were less than 1/10th as toxic as TBT and they did not have a chemotactic effect on either organism at concentrations at which TBT had a significant effect. Therefore, both the Sn-and butyl-moieties contribute to the toxic and chemotactic properties of TBT.     

Microbial transformations of tin and tin compounds

Summary The use of organotins for agricultural and industrial purposes and in the marine environment has been increasing steadily for more than 20 years. Recently, reliable methodologies have been developed to permit quantification of individual molecular species of organotins in cultures and in the environment. Particular attention has been given to methyltins which can be formed abiotically and by microorganisms, and to tributyltins which are toxic components of effective antifouling paints. In the aquatic environment tin, tributyltins and other organotins accumulate in the surface microlayer, in sediments, and on suspended particulates. Tin compounds are toxic to a variety of organisms and some aquatic organisms can bioaccumulate them. When tin compounds, particularly di-or tri-substituted tins, enter an ecosystem, a portion of the microbial population is killed. Among the survivors are organisms which can methylate inorganic or organic tins, but the relative contribution of biotic and abiotic mechanisms is not clear. While many details of methylations and demethylations need to be worked out, it is clear that transformations of tins can influence the toxicity, volatility and mobility of tin in natural ecosystems. Tributyltins can be debutylated by microorganisms, and hydroxybutyl tins may be intermediates, as they are in mammalian systems. Little is known of the potential and probable microbial transformations of other economically important organotins, but the transformations should be studied for they may have industrial and environmental importance.     

Resistance to arsenic compounds in microorganisms

Abstract: Arsenic ions, frequently present as environmental pollutants, are very toxic for most microorganisms. Some microbial strains possess genetic determinants that confer resistance. In bacteria, these determinants are often found on plasmids, which has facilitated their study at the molecular level. Bacterial plasmids conferring arsenic resistance encode specific efflux pumps able to extrude arsenic from the cell cytoplasm thus lowering the intracellular concentration of the toxic ions. In Gram-negative bacteria, the efflux pump consists of a two-component ATPase complex. ArsA is the ATPase subunit and is associated with an integral membrane subunit, ArsB. Arsenate is enzymatically reduced to arsenite (the substrate of ArsB and the activator of ArsA) by the small cytoplasmic ArsC polypeptide. In Gram-positive bacteria, comparable arsB and arsC genes (and proteins) are found, but arsA is missing. In addition to the wide spread plasmid arsenic resistance determinant, a few bacteria confer resistance to arsenite with a separate determinant for enzymatic oxidation of more-toxic arsenite to less-toxic arsenate. In contrast to the detailed information on the mechanisms of arsenic resistance in bacteria, little work has been reported on this subject in algae and fungi.     

1,8-二羟基蒽醌对大型溞的毒性效应

The study on the acute,sublethal and chronic toxicity of 1,8-dihydroxyanthraquinone (1,8-dihAQ) to Daphnia magna showed that the 48 h LC₅₀ was 0.37 mg稬^-1,and the feeding behavior of Daphnia magna was severely affected by the compound.When exposed to 0.2 mg稬^-1 of 1,8-dihAQ for 5 h,the filtration and ingestion rate of Daphnia magna was inhibited by 97%.Chronic toxicity test results indicated that the reproduction ability decreased dramatically after exposing to sublethal concentration of 1,8-dihAQ.It could be inferred that reproduction parameters and intrinsic rate of natural increase were the sensitive parameters in characterizing sublethal toxicity.The NOEC and LOEC values for reproduction parameters were also given.     

The influence of tin compounds on the dynamic properties of liposome membranes: A study using the ESR method

The influence of organic and inorganic compounds of tin on the dynamic properties of liposome membranes obtained in the process of dipalmitoylphosphatidylcholine (DPPC) sonication in distilled water was investigated. This was carried out by means of the spin ESR probe method. The probes were selected in such a way as to penetrate different areas of the membrane (a TEMPO probe, 5-DOXYL stearic acid, 16-DOXYL stearic acid). Four compounds of tin were chosen: three organic ones, (CH₃)₄Sn, (C₂H₅)₄Sn and (C₃H₇)₃SnCl, and one inorganic one, SnCl₂. The investigated compounds were added to a liposome dispersion, which was prepared prior to that. The concentration of the admixture was changed within the values from 0 to 10%-mole in proportion to DPPC. The studies indicated that the chlorides of tin display the highest activity in their interaction with liposome membranes. Since these compounds have ionic form in a water solution, the obtained result can mean that this form of admixture has a considerable influence on its activity. Furthermore, it was found that there is a slightly stronger influence of tin compounds with a longer hydrocarbon chain on changes in the probes’ spectroscopic parameters.     

Toxic effects of dichloromethane on the growth of methanotrophic bacteria

Abstract The effect of a range of dichloromethane (DCM) concentrations on the growth of five obligate methanotrophic bacteria of the genera Methylomonas, “Methylosinus” , and Methylocystis was assessed. DCM concentrations of 78 mM were bactericidal for all strains. Concentrations of 7.8 mM–156 μM were bacteriostatic for Methylocystis parvus ACM 3309 and Methylomonas aurantiaca HB2, and partially inhibitory for Methylomonas methanica strains ACM 3307 and HB1. “Methylosinus trichosporium” ACM 3311 grew in the presence of up to 780 μm DCM, but a concentration of 7.8 mM was bacteriostatic.     

Toxic effects of thiol-reactive compounds on anaerobic biomass

The objective of this study was to characterize the toxic effects of three well known thiol-reactive electrophilic compounds, N-ethylmaleimide (NEM), pentachlorophenol (PCP) and 1-chloro-2,4-dinitrobenzene (CDNB) on anaerobic biotransformation process. The work was part of a larger investigation on potassium efflux as a possible response mechanism of anaerobic microorganisms to the presence of thiol-reactive organic compounds and the interference of such compounds on the reductive dehalogenation process. Using anaerobic toxicity assay (ATA) and granular anaerobic biomass from a full-scale upflow anaerobic sludge blanket (UASB) reactor, inhibitory concentrations of these compounds that reduced the microbial activity of granular biomass to 50% of a control (IC50) were determined to be 592, 0.97, and 450 mg/l for NEM, PCP, and CDNB, respectively. Toxicity of NEM was also tested on anaerobic biomass from a municipal wastewater treatment plant digester and slightly lower IC50 of 532 mg/l was obtained. The results presented here indicate that anaerobic biomass can acclimate to the three thiol-reactive compounds studied and recover from inhibition as long as the toxicant concentration is below a threshold level. That threshold concentration was found to be 500 mg/l for NEM on biomass from the municipal digester, 1 mg/l for PCP, and 500 mg/l for CDNB, both on granular biomass. Granular anaerobic biomass showed recovery even at NEM concentrations of 1000 mg/l.     

Toxic effects of chromium and its compounds

Chromium was discovered in 1797 by Vauquelin. Numerous industrial applications raised chromium to a very important economic element. At the same time, with the development of its uses, the adverse effects of chromium compounds in human health were being defined. Trivalent chromium is an essential trace element in humans and in animals. Chromium as pure metal has no adverse effect. Little toxic effect is attributed to trivalent chromium when present in very large quantities. Both acute and chronic toxicity of chromium are mainly caused by hexavalent compounds. The most important toxic effects, after contact, inhalation, or ingestion of hexavalent chromium compounds are the following: dermatitis, allergic and eczematous skin reactions, skin and mucous membrane ulcerations, perforation of the nasal septum, allergic asthmatic reactions, bronchial carcinomas, gastro-enteritis, hepatocellular deficiency, and renal oligo anuric deficiency. Prevention of occupational risks, biological monitoring of workers, and treatment of poisoning are also reported.     

Synthesis and reactivity of tin amide complexes

A terminal tin amide and a terminal tin anilide complex, (BDI)SnN(iPr₂) and (BDI)SnN(H)Ar (Ar = 2,6-ⁱPr₂C₆H₃), respectively, have been synthesized utilizing the bulky β-diketiminate ligand, [{N(2,6-ⁱPr₂C₆H₃)C(Me)}₂CH]⁻, or BDI, to stabilize the low coordinate divalent tin metal center. Only (BDI)SnN(iPr₂) reacts with phenylacetylene to yield (BDI)SnCCPh, but both species react with methyl triflate to give (BDI)SnOTf and carbon dioxide, resulting in the formation of (BDI)SnOC(O)N(iPr₂) and (BDI)SnOC(O)N(H)Ar.     

Toxic effects of chlorpyrifos on the growth,hematology, and different organs histopathology of Nile tilapia,Oreochromis niloticus

Chlorpyrifos is a widely applied insecticide that permeates on most waterways and affects aquatic organisms. The growth performances, hematological and histological impacts on Nile tilapia, Oreochromis niloticus following a 60 day of exposure to varying concentrations of chlorpyrifos 20 EC (T₁ 08 µgL^?1, T₂ 16 µgL^?1, and T₃ 32 µgL^?1) were compared to a control T_c 0 µgL^?1. The 96-hour LC50 of chlorpyrifos 20 EC was calculated as 46.80 μgL^?1. The water quality parameters were recorded regularly. The value of dissolved O₂ and NH₃ stayed rather steady, although temperature varied considerably. It was revealed that as chlorpyrifos levels go up, the percentage of weight gain (WG %), specific growth rates (SGR), and survival rate decreases. The control group T_c had the highest percentages of SGR weight (1.16 ± 0.58) and the T₃ group had the lowest percentages of SGR weight (0.25 ± 0.77). The hematological assessment showed significant differences of hemoglobin concentration, white blood cell counts and red blood cell numbers between chlorpyrifos treatment and control group (P < 0.05). Histological alterations in the liver, gills, and muscle tissues reported to be worse for T₃ as compared to others. There were no statistical differences in GSI, HSI values between control and treatment groups. The chlorpyrifos 20 EC was shown to be highly toxic to O. niloticus at sub-lethal dosages.     

Enrichment with a polyunsaturated fatty acid enhances the survival of Saccharomyces cerevisiae in the presence of tributyltin

The toxicity of inorganic metal species towards Saccharomyces cerevisiae has been shown to be markedly dependent on cellular fatty acid composition. In this investigation, the influence of fatty acid supplementation on the toxicity of the lipophilic organometal, tributyltin was investigated. Growth of S. cerevisiae was increasingly inhibited when the tributyltin concentration was increased from 0 to 10 μM. However, the inhibitory effect was partly alleviated by supplementation of the medium with 1 mM linoleate (18:2), a treatment that leads to large-scale incorporation of this polyunsaturated fatty acid (to >60% of total fatty acids) in yeast membrane lipids. Cells that were previously enriched with 18:2 also showed reduced loss of vitality compared to cells grown in the absence of a fatty acid supplement, when exposed to tributyltin. For example, addition of tributyltin to a concentration of 0.1 μM was associated with an approximate 10% reduction in the H⁺ efflux activity of 18:2-enriched cells, but a 70% reduction in that of fatty acid-unsupplemented cells. Despite the increased tributyltin resistance of 18:2-enriched S. cerevisiae, the level of cell-associated tributyltin was found to be approximately two-fold higher in these organisms than in fatty acid-unsupplemented cells. These results demonstrate an increased resistance of 18:2-enriched membranes to the direct toxic action(s) of tributyltin. This is in contrast to the previously reported effect of 18:2 enrichment on sensitivity of S. cerevisiae to inorganic metal cations.     

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.     

尼古丁对牙周炎大鼠牙周膜成纤维细胞的毒性作用

目的:观察尼古丁对牙周炎大鼠牙周膜成纤维细胞(PDLFs)增殖的抑制作用及对细胞周期分布的影响,探讨尼古丁的细胞毒性作用,为口腔疾病的预防及治疗提供基础。方法:选取30只SD大鼠,采用丝线结扎联合口内接种细菌的方法建立牙周炎大鼠模型。将不同浓度的尼古丁分别作用于大鼠的牙周膜成纤维细胞(PDLFs)中,观察大鼠牙周组织的变化情况,MTT法测定细胞增殖活性,分析不同浓度尼古丁对PDLFs增殖的抑制作用。结果:实验组大鼠牙周组织胶原纤维束排列紊乱,有炎症细胞浸润;对照组大鼠牙龈未见红肿或出血。尼古丁可抑制PDLFs增殖,并且呈浓度依赖性,随着浓度的增加,对PDLFs增殖的抑制作用增强,差异具统计学意义(P0.05)。与对照组相比,不同浓度尼古丁作用下牙周炎大鼠牙周膜成纤维细胞周期的分布率明显不同(P0.05)。结论:尼古丁对牙周膜成纤维细胞增殖具有明显的抑制作用,尼古丁的浓度影响牙周组织的修复重构能力。     

微生物来源的抗植物病毒活性物质研究进展

近年来,研究者利用微生物及其次生代谢产物开展了大量防治植物病毒病的研究,从中发现了许多具有抗植物病毒活性的大分子物质及小分子化合物。本文对来源于不同种类微生物的抗病毒活性物质及抗病毒机理作了论述,并对微生物来源抗植物病毒物质研究进行了展望,以期为开发用于植物病毒病防治的微生物农药提供借鉴。     

Copper toxicity and uptake in microorganisms

Summary Copper is a required trace element for growth of microorganisms since it is a cofactor for numerous enzymes. Also, proteins containing copper are important electron transfer carriers. However, at elevated concentrations, copper can be highly toxic to microorganisms. This review examines copper toxicity and uptake in microorganisms, with an emphasis on copper-resistance mechanisms.