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At least 19 recordsLinked to original sources

Interactions of cyclic hydrocarbons with biological membranes.

Many cyclic hydrocarbons, e.g. aromatics, cycloalkanes, and terpenes, are toxic to microorganisms. The primary site of the toxic action is probably the cytoplasmic membrane, but the mechanism of the toxicity is still poorly understood. The effects of cyclic hydrocarbons were studied in liposomes prepared from Escherichia coli phospholipids. The membrane-buffer partition coefficients of the cyclic hydrocarbons revealed that these lipophilic compounds preferentially reside in the membrane. The partition coefficients closely correlated with the partition coefficients of these compounds in a standard octanol-water system. The accumulation of hydrocarbon molecules resulted in swelling of the membrane bilayer, as assessed by the release of fluorescence self-quenching of fluorescent fatty acid and phospholipid analogs. Parallel to the expansion of the membrane, an increase in membrane fluidity was observed. These effects on the integrity of the membrane caused an increased passive flux of protons and carboxyfluorescein. In cytochrome c oxidase containing proteoliposomes, both components of the proton motive force, the pH gradient and the electrical potential, were dissipated with increasing concentrations of cyclic hydrocarbons. The dissipating effect was primarily the result of an increased permeability of the membrane for protons (ions). At higher concentrations, cytochrome c oxidase was also inactivated. The effective concentrations of the different cyclic hydrocarbons correlated with their partition coefficients between the membrane and aqueous phase. The impairment of microbial activity by the cyclic hydrocarbons most likely results from hydrophobic interaction with the membrane, which affects the functioning of the membrane and membrane-embedded proteins.

Benzene↗

Antioxidant and detoxifying enzymes in the liver of rats after subchronic inhalation of the mixture of cyclic hydrocarbons.

The activity of antioxidant and detoxifying enzymes, superoxide dismutase (SOD), glutathione peroxidase (GSHPx), glutathione-S-transferase (GST), the SOD isoenzyme patterns and the contents of thiobarbituric acid reactive substances (TBARS), were determined in the livers of male and female rats after subchronic inhalation of mixtures of benzene, cyclohexanone and cyclohexane. Except for decreased GSHPx (with substrate cumene hydroperoxide) and GST activities in female rats, no differences in the activities of antioxidant and detoxifying enzymes and TBARS content occurred. Between the activities of GSHPx and GST was observed an indirect relationship. The activities of GSHPx-cum and GST were influenced by sex.

Animals↗

Planar tetracoordinate carbons in cyclic hydrocarbons.

[structure: see text] A series of cyclic hydrocarbons containing a planar tetracoordinate carbon atom is proposed. To rationalize the electronic factors contributing to the stability of these molecules, an analysis of the molecular orbitals and the induced magnetic field is presented.

Journal Article↗

Oxidation of alkyl-substituted cyclic hydrocarbons by a Nocardia during growth on n-alkanes.

Nocardia 107-332, a soil isolate, oxidizes short-chain alkyl-substituted cyclic hydrocarbons to cyclic acids while growing on n-alkanes. Cyclic acids are produced also from relatively long-chain alkyl-substituted cyclics such as n-nonylbenzene or n-dodecylbenzene which alone support growth in a mineral-salts medium. omega-Oxidation of the alkyl substituents is followed by beta-oxidation. It is of particular interest that cyclic acids such as cyclohexaneacetic and phenylacetic with C(2) residual carboxylic acid substituents are resistant to further oxidation by the nocardia but cyclic acids with C(1) or C(3) substituents are readily oxidized and utilized for growth. The specificity of microbial oxidations is demonstrated by the conversion of p-isopropyltoluene (p-cymene) to p-isopropylbenzoic acid in n-alkane, growth-supported nocardia cultures.

Alkanes↗

Topographic recognition of cyclic hydrocarbons and related compounds by receptors for androgens, estrogens, and glucocorticoids.

The structural requirements for the interaction of about 80 cyclic hydrocarbons and related compounds with the androgen receptor of rat ventral prostate, the estrogen receptor of human breast tumor MCF-7 cells, and the glucocorticoid receptor of rat liver were examined by comparing their abilities to compete with radioactive hormones for binding to the respective receptors. The results indicate that the receptor-binding affinity of a compound is dependent on its electronic configuration and geometrical similarity to a portion of a natural steroid hormone which can be recognized by local ligand-binding sites in the receptor. For the estrogen receptor, beta-phenols are more active than the corresponding alpha-phenols, whereas nonphenolic compounds are totally inactive. For androgen and glucocorticoid receptors, alpha-phenols are more active than beta-phenols. The androgen receptor can interact stereospecifically with nonoxygenated and nonalkylated cyclic hydrocarbons, such as 10,11-dihydro-5H-dibenzo[a,d] cycloheptene or 9,10-dihydrophenanthrene, which can, in vivo, inhibit the androgen-dependent growth of the male accessory reproductive organs. The affinities of naphthalene, anthracene, phenanthrene, biphenyl, and adamantane toward glucocorticoid and androgen receptors can be enhanced by acetylation or ethanolization of these ligands. Our results also indicate that, while the hormonal action of a steroid may be dependent on the interaction of a functional group on the hormone with a specific group on the receptor, the presence of such a group may not be required for the antagonistic activity of a compound that can physically block hormone binding to the receptor. Thus, many small molecules that were hitherto considered to be biologically inert may interact with steroid receptors specifically and affect hormonal activities in vivo.

Animals↗

[The lipid peroxidation system in the organism of experimental animals after exposure to cyclic hydrocarbons].

The paper presents the results of studies of the amounts of diene conjugates, malonic dialdehyde, and Schiff's bases, which are molecular LPO products in the tissues of the lung, liver, kidney in animals exposed to 4-hour inhalation of cyclic hydrocarbons (pyromellitic dianhydride, durol, pseudocumene, and dioxane-1,4). Exposure to ecotoxicants at concentrations of 10 and 1 mg/m3 was found to result in the accumulation of initial, intermediate, and final molecular LPO products. These changes were recorded only after exposure to pseudocumene and dioxane vapors in a dose of 0.1 mg/m3 and after inhalation of dioxane-1,4 vapors in a dose of 0.01 mg/m3.

Administration, Inhalation↗

Non-enzymatic and microsome-dependent binding of poly-cyclic hydrocarbons to DNA and polynucleotides.

The binding of tritium-labeled 7,12-dimethylbenz[a]anthracene (DMBA), benzo[a]pyrene (BP) and 3-methylcholanthrene (MCA) to DNA or polynucleotides in vitro was re-examined both in the presence and in the absence of rat liver or human placental microsomes. A high level of non-enzymatic binding was evident when thymus DNA was used as acceptor. This non-enzymatic binding made it difficult to determine the effect of microsomes, except in the case of BP when induced rat microsomes were used. Better results were obtained using polynucleotides: a definite microsome-dependent binding occurred between all the polynucleotides and all the hydrocarbons tested. No clear evidence of binding catalysed by microsomes from human placenta was found except in polynucleotide-BP interactions: further studies are required to completely evaluate the ability of such nucleic acid-microsomal system for testing in vitro possible oncogenic substances in animals and humans.

9,10-Dimethyl-1,2-benzanthracene↗

Interfacial properties of cyclic hydrocarbons: a Monte Carlo study.

The Monte Carlo technique is used to study the vapor-liquid interface of cyclopentane, cyclohexane, and benzene. The OPLS and TraPPE potential fields are compared in the temperature range from 298.15 to 348.15 K (273.15-298.15 K for C5H10). A new method for the treatment of the long-range interactions in inhomogeneous simulations is used. When this new method is employed, the obtained values of saturated liquid density and of enthalpy of vaporization are equal to those obtained using the bulk isothermal-isobaric Monte Carlo technique. The values of surface tension become independent of the cutoff distance and they are significantly larger than those when only simple spherical truncation of intermolecular interactions is used.

Journal Article↗

Determination of organic contaminants in residential indoor air using an adsorption-thermal desorption technique.

This field study evaluated the ability of a multi-sorbent sampling tube/thermal desorption technique to identify and to provide quantitative data on volatile organic contaminants in indoor air. Air samples, from 12 Canadian homes, were collected on multilayer sorbent cartridges and analyzed using Adsorption/Thermal Desorption coupled with Gas Chromatography/Mass Spectrometry. The study included the identification and quantitation of 23 target compounds. Analysis of sorbent tubes fortified with these target compounds indicated that recoveries were greater than 70 percent and the precision was usually better than 15 percent. These organic compounds were found to be stable on the sorbent tubes for at least seven days. With some exceptions, the target compounds were usually detected at 1 to 10 micrograms/m3 in indoor air samples; other organics identified qualitatively were saturated hydrocarbons, unsaturated hydrocarbons, cyclic hydrocarbons, substituted aromatics, oxygenates, some halogenates and cyclic species such as camphenes/pinenes and carenes.

Adsorption↗

Sonochemical reaction of selected cyclic C6Hx hydrocarbons in organic solvents.

The rates and products of the sonochemical reactions of benzene, 1,4-cyclohexadiene, 1,3-cyclohexadiene, cyclohexene, and cyclohexane in selected organic solvents have been investigated. The sonochemical reactions of these educts in the investigated organic solvents follow first-order kinetics. Generally, they are sonicated more rapidly in polar than in non-polar solvent; higher volatility of the solute results in faster sonolysis in the organic solvents. However, the sonication of cyclohexane in n-decane and the sonication of benzene in n-propanol are exceptional cases. Since cyclohexane exhibits a much higher lipophilicity and benzene a much higher hydrophilicity than other educts, it might be more difficult to transfer either educt from the bulk liquid into the cavitation bubbles. In tetrachloroethylene, the reactivity of the tested educts with in situ generated chlorine as well as chlorine-containing radical intermediates can accelerate the rate of sonochemical reactions under the employed conditions. In n-propanol and n-decane, the pyrolysis during the collapse of the cavitation bubbles is the only reaction pathway of sonolysis. In tetrachloroethylene, the pyrolysis during the collapse of the cavitation bubbles and the free radical reaction in the bulk liquid may occur simultaneously. Except for the products generated from sonolysis, products formed from chlorine transformations (substitution or addition reactions) are detected. Benzene is hardly decomposed in tetrachloroethylene. However, when FeCl3 is added into the reaction system, benzene is sonoconverted rapidly, and the product chlorobenzene was detected. In organic solvents, the sonoreaction rates and the sonoproducts are dependent on the physicochemical properties of the solvents used, as well as the volatility, the polarity and the reactivity of educts.

Hydrocarbons, Cyclic↗

A chemical definition of the effective reducing power of thulium(II) diiodide by its reactions with cyclic unsaturated hydrocarbons.

Thulium diiodide reduces cyclic aromatic hydrocarbons that have reduction potentials more positive than - 2.0 V versus SCE. Thus, TmI2 reacts with cyclooctatetraene or acenaphthylene in THF, or with lithium anthracenide in 1,2-dimethoxyethane (DME) to give thulium triiodide and the thulium(III) complexes [(eta8-C8H8)TmI(thf)2] (1), rac-ansa-[(eta5-C12H8)2TmI(thf)] (2), or [(eta2-C14H10)TmI-(dme)2] (3), respectively. The molecular structures of 1-3 were determined by single-crystal X-ray diffraction.

Journal Article↗

Benzene formation during aquasonolysis of selected cyclic C6Hx hydrocarbons.

Yield and selectivity of benzene produced from aquasonolysis of the selected cyclic C6Hx hydrocarbons, i.e., 1,4-cyclohexadiene, 1,3-cyclohexadiene, cyclohexene, cyclohexane, and methylcyclopentane, have been investigated in this work. Benzene cannot be detected during the aquasonolysis of cyclohexane and methylcyclopentane. The order of yield and selectivity of benzene was as follows: 1,4-cyclohexadiene>>1,3-cyclohexadiene>>cyclohexene. The initial concentrations of substrates can affect the yield of benzene. During the aquasonolysis of 1,3-cyclohexadiene and cyclohexene, other C6 species except benzene were also found. It was suggested that benzene could directly be generated by formal dehydrogenation of cyclic C6Hx hydrocarbons.

Benzene↗

Towards design of the smallest planar tetracoordinate carbon and boron systems.

A series of cyclic hydrocarbons analogs where a carbon displays unusual planar tetracoordinate structure is proposed, employing hybrid density functional theory calculations using B3LYP functional and 6-311+G** basis set. Various strategies were employed to design the neutral planar tetracoordinate hydrocarbon analogs. The same strategy is employed for designing the planar tetracoordinate boron systems. The simplest neutral planar tetracoordinate hydrocarbons were proposed and the effect of substitution on their stability has been assessed. The aromatic stabilization is gauged with nucleus independent chemical shift calculations. The activation barriers for the ring opening reaction, the highest occupied molecular orbital and lowest unoccupied molecular orbitals gap and singlet-triplet energy difference were estimated to gauge the plausibility experimental realization.

Boron↗