Sporostatic and Sporocidal Properties of Aqueous Formaldehyde

Aqueous formaldehyde is shown to exert both sporostatic and sporocidal effects on Bacillus subtilis spores. The sporostatic effect is a result of the reversible inhibition of spore germination occasioned by aqueous formaldehyde; the sporocidal effect is due to temperature-dependent inactivation of these spores in aqueous formaldehyde. The physicochemical state of formaldehyde in solution provides a framework with which to interpret both the sporostatic and sporocidal properties of aqueous formaldehyde.     

The Relationship between Structure and Activity of Taurolin

Taurolin [Bis(1,1-dioxo-perhydro-1,2,4 thiadiazinyl-4)methane] is an antimicrobial compound formed by the condensation of two molecules of taurine with three of formaldehyde. It has been suggested that it releases formaldehyde in contact with bacteria. Evidence from TLC, HPLC and NMR spectroscopy indicates that taurolin is mostly hydrolysed in aqueous solution to release one molecule of formaldehyde and two monomeric molecules (1,1-dioxo-perhydro-1,2,4-thiadiazine and its carbinolamine derivative). A stable equilibrium is established. Antibacterial activity is not entirely due to adsorption of free formaldehyde but also to reaction with a masked (or latent) formaldehyde, as the activity of taurolin is greater than formaldehyde. The monomer is only slightly active by comparison.     

Denaturation of deoxyribonucleic acid in situ effect of formaldehyde.

In situ denaturation of nuclear deoxyribonucleic acid (DNA) is studied by use of acridine orange to differentially stain native versus denatured DNA, and a flow-through cytofluorometer for measurements of cell fluorescence. Thermal- or acid-induced DNA denaturation is markedly influenced by formaldehyde. Two mechanisms of the formaldehyde action are distinguished. If cells are exposed to the agent during heating, DNA denaturation is facilitated, most likely by the direct action of formaldehyde as a "passive" denaturing agent on DNA. If cells are pretreated with formaldehyde which is then removed, DNA resistance to denaturation increases, presumably due to chromatin cross-linking. It is believed that both effects occur simultaneously in conventional techniques employing formaldehyde to study DNA in situ, and that the extent of each varies with the temperature and cell type (chromatin condensation). Thus, profiles of DNA denaturation of cells heated with formaldehyde do not represent characteristics of DNA denaturation in situ; DNA denaturation under these conditions is modulated by the reactivity of chromatin components with formaldehyde rather than by DNA interactions with the macromolecules of nuclear mileu.     

Inhibition of CO2 production from aminopyrine or methanol by cyanamide or crotonaldehyde and the role of mitochondrial aldehyde dehydrogenase in formaldehyde oxidation

Previous results have shown that cyanamide or crotonaldehyde are effective inhibitors of the oxidation of formaldehyde by the low-Km mitochondrial aldehyde dehydrogenase, but do not affect the activity of the glutathione-dependent formaldehyde dehydrogenase. These compounds were used to evaluate the enzyme pathways responsible for the oxidation of formaldehyde generated during the metabolism of aminopyrine or methanol by isolated hepatocytes. Both cyanamide and crotonaldehyde inhibited the production of 14CO2 from 14C-labeled aminopyrine by 30-40%. These agents caused an accumulation of formaldehyde which was identical to the loss in CO2 production, indicating that the inhibition of CO2 production reflected an inhibition of formaldehyde oxidation. The oxidation of methanol was stimulated by the addition of glyoxylic acid, which increases the rate of H2O2 generation. Crotonaldehyde inhibited CO2 production from methanol, but caused a corresponding increase in formaldehyde accumulation. The partial sensitivity of CO2 production to inhibition by cyanamide or crotonaldehyde suggests that both the mitochondrial aldehyde dehydrogenase and formaldehyde dehydrogenase contribute towards the metabolism of formaldehyde which is generated from mixed-function oxidase activity or from methanol, just as both enzyme systems contribute towards the metabolism of exogenously added formaldehyde.     

Growth of Pseudomonas C on C1 compounds: enzyme activites in extracts of Pseudomonas C cells grown on methanol, formaldehyde, and formate as sole carbon sources.

Pseudomonas C can grow on methanol, formaldehyde, or formate as sole carbon source. It is proposed that the assimilation of carbon by Pseudomonas C grown on different C1 growth substrates proceeds via one of two metabolic pathways, the serine pathway or the allulose pathway (the ribose phosphate cycle of formaldehyde fixation). This contention is based on the distribution of two key enzymes, each of which appears to be specifically involved in one of the assimilation pathways, glycerate dehydrogenase (serine pathway) and hexose phosphate synthetase (allulose pathway). The assimilation of methanol in Pseudomonas C cells appears to occur via the allulose pathway, whereas the utilization of formaldehyde or formate in cells grown on formaldehyde or formate as sole carbon sources appears by the serine pathway. When methanol is present together with formaldehyde or formate in the growth medium, the formaldehyde or formate is utilized by the allulose pathway.     

The cellular function and molecular mechanism of formaldehyde in cardiovascular disease and heart development

As a common air pollutant, formaldehyde is widely present in nature, industrial production and consumer products. Endogenous formaldehyde is mainly produced through the oxidative deamination of methylamine catalysed by semicarbazide-sensitive amine oxidase (SSAO) and is ubiquitous in human body fluids, tissues and cells. Vascular endothelial cells and smooth muscle cells are rich in this formaldehyde-producing enzyme and are easily damaged owing to consequent cytotoxicity. Consistent with this, increasing evidence suggests that the cardiovascular system and stages of heart development are also susceptible to the harmful effects of formaldehyde. Exposure to formaldehyde from different sources can induce heart disease such as arrhythmia, myocardial infarction (MI), heart failure (HF) and atherosclerosis (AS). In particular, long-term exposure to high concentrations of formaldehyde in pregnant women is more likely to affect embryonic development and cause heart malformations than long-term exposure to low concentrations of formaldehyde. Specifically, the ability of mouse embryos to effect formaldehyde clearance is far lower than that of the rat embryos, more readily allowing its accumulation. Formaldehyde may also exert toxic effects on heart development by inducing oxidative stress and cardiomyocyte apoptosis. This review focuses on the current progress in understanding the influence and underlying mechanisms of formaldehyde on cardiovascular disease and heart development.     

Biodegradation of high concentrations of formaldehyde by lyophilized cells of Methylobacterium sp. FD1

In the present study, Methylobacterium sp. FD1 utilizing formaldehyde was isolated from soil. The resting cells of FD1 degraded high concentrations of formaldehyde (~2.7 M) and produced formic acid and methanol that were molar equivalents of one-half of the degraded formaldehyde. This result suggests that formaldehyde degradation by FD1 is caused by formaldehyde dismutase. The optimal temperature and pH for formaldehyde degradation by the resting cells of FD1 were 40 °C and 5–7, respectively. The lyophilized cells of FD1 also degraded high concentrations of formaldehyde. The formaldehyde degradation activity of the lyophilized cells was maintained as the initial activity at 25 °C for 287 days. These results suggest that the lyophilized cells of FD1 are useful as formaldehyde degradation materials.     

Effect of acetaldehyde and cyanamide on the metabolism of formaldehyde by hepatocytes, mitochondria, and soluble supernatant from rat liver

Formaldehyde can be metabolized primarily by two different pathways, one involving oxidation by the low-Km mitochondrial aldehyde dehydrogenase, the other involving a specific, glutathione-dependent, formaldehyde dehydrogenase. To estimate the roles played by each enzyme in formaldehyde metabolism by rat hepatocytes, experiments with acetaldehyde and cyanamide, a potent inhibitor of the low-Km aldehyde dehydrogenase were carried out. The glutathione-dependent oxidation of formaldehyde by 100,000g rat liver supernatant fractions was not affected by either acetaldehyde or by cyanamide. By contrast, the uptake of formaldehyde by intact mitochondria was inhibited 75 to 90% by cyanamide. Acetaldehyde inhibited the uptake of formaldehyde by mitochondria in a competitive fashion. Formaldehyde was a weak inhibitor of the oxidation of acetaldehyde by mitochondria, suggesting that, relative to formaldehyde, acetaldehyde was a preferred substrate. In isolated hepatocytes, cyanamide, which inhibited the oxidation of acetaldehyde by 75 to 90%, produced only 30 to 50% inhibition of formaldehyde uptake by cells as well as of the production of 14CO2 and of formate from [14C]formaldehyde. The extent of inhibition by cyanamide was the same as that produced by acetaldehyde (30-40%). In the presence of cyanamide, acetaldehyde was no longer inhibitory, suggesting that acetaldehyde and cyanamide may act at the same site(s) and inhibit the same formaldehyde-oxidizing enzyme system. These results suggest that, in rat hepatocytes, formaldehyde is oxidized by cyanamide- and acetaldehyde-sensitive (low-Km aldehyde dehydrogenase) and insensitive (formaldehyde dehydrogenase) reactions, and that both enzymes appear to contribute about equally toward the overall metabolism of formaldehyde.     

2012年食用菌“平菇甲醛”事件浅析

对2012年4月媒体报道的青岛平菇中检测发现甲醛所引发的争论进行了剖析。综合分析国内外对食用菌和其他天然食品中甲醛含量的研究结果,以及甲醛自身的理化特性,作者认为食用菌中含有微量甲醛是食用菌自身新陈代谢的产物,从食品安全的角度考虑是安全的。文中介绍了国内外对部分食用菌中甲醛含量的测定、代谢机理和风险评估情况,其中食用菌甲醛的代谢机理值得进一步关注和探讨。     

Analysis of the Reaction between Formaldehyde and Amide

The reaction between formaldehyde and acetamide which affords a model compound for an amino acid having an amide group was analyzed to investigate the role of formaldehyde as a cross-linking reagent. One of the products was isolated by Sephadex G-10 column chromatography and was identified as N-hydroxymethyl acetamide (FA) by NMR spectrometry and mass spectrometry. Another product, which could not be isolated, was estimated to be N, N-dihydroxymethyl acetamide (F₂A) by kinetic analysis and mass spectrometry. The formation of N, N′-methylene diacetamide was not observed. The mechanism of the reaction between formaldehyde and acetamide was estimated by the kinetic analyses of NMR data, and the rate constants were calculated from the data by the optimization method with a digital computer. On the other hand, formaldehyde cross-linked product was obtained in the reaction of formaldehyde with acetamide and alanine, Its decomposing reaction was analyzed with an NMR spectrometer to study the stability of the formaldehyde cross-linked product. The degradation was dominantly initiated with the release of acetamide.

Consequently, it was estimated that the C–N bond between formaldehyde and amide is so labile that amide-bound formaldehyde does not react further with amides or amines, and that the amide-formaldehyde-amine condensation product is unstable and easily decomposes by releasing the amide.     

The mechanism of microbial resistance to hexahydro-1,3,5-triethyl-s-triazine

Summary Four strains ofPseudomonas putida and two unidentifiedPseudomonas species that were resistant to hexahydro-1,3,5-triethyl-s-triazine (HHTT) were shown to be resistant to formaldehyde as well. Conjugation experiments revealed that: (a) HHTT and formaldehyde resistance was cotransferred in every case where exconjugants were recovered; (b) in every case HHTT resistance and formaldehyde resistance were expressed to the same level in the exconjugant as in the donor; (c) resistance to either HHTT or formaldehyde alone was never observed; and (d) in instances where HHTT and formaldehyde resistance in the exconjugants was unstable, the exconjugants lost resistance to both agents simultaneously and never to one agent alone. Resistant organisms (e.g.P. putida 3-T-15²) had high levels of formaldehyde dehydrogenase and this enzyme appeared to be constitutively expressed. It was concluded that resistance to HHTT was due to resistance to its degradation product, formaldehyde, via detoxification of formaldehyde by formaldehyde dehydrogenase. HHTT- and formaldehyde-sensitive organisms had barely detectable levels (most likely repressed levels) of formaldehyde dehydrogenase. Although speculative, it is possible that formaldehyde resistance may be due to a mutation resulting in derepression of the gene coding for formaldehyde dehydrogenase. While it could not be discerned whether HHTT resistance and formaldehyde resistance were carried on two separate but closely linked genes or if only one gene was involved, the evidence suggested that only one gene was involved. Similarly, it could not be determined whether HHTT and formaldehyde resistance was encoded by chromosomal or plasmid genes.     

Hepatic organelle interaction. IV. Mechanism of succinate enhancement of formaldehyde accumulation from endoplasmic reticulum N-dealkylations

Further evidence for organelle interaction during drug metabolism by the liver is presented. The apparent stimulation by succinate of formaldehyde accumulation in the medium, which was reported to occur with liver slices and homogenates as well as with mitochondria plus microsomes, has been shown to be the result of succinate inhibition of mitochondrial aldehyde dehydrogenase. The mechanism of succinate inhibition is shown to be by reverse electron transport, and an increase in the NADH to NAD+ ratio in the mitochondria; the aldehyde dehydrogenase requires the oxidized form of the pyridine nucleotide as its cofactor. Studies on in vitro N-demethylation by liver microsomes and endoplasmic reticulum segments which cosediment with the mitochondria indicate that formaldehyde produced by the mixed function oxidase is handled differently from formaldehyde added to the medium. The latter is mainly retained in the medium containing 5 mM semicarbazide, while the generated formaldehyde is more than 50% consumed by the mitochondria. Electron microscopy has indicated that the microsomes and the endoplasmic reticulum fragments have a tendency to align themselves close to the mitochondria when present in the same medium. Consequently, it is possible that formaldehyde released to the medium adjacent to the mitochondria, as by N-demethylation, would be exposed to semicarbazide for shorter periods than that added directly to the medium. In agreement with this suggestion, complexing of formaldehyde with semicarbazide was observed spectroscopically not to be an extremely rapid reaction even at 37 degrees C. This is believed to be the reason for the greater extent of consumption of formaldehyde generated by the endoplasmic reticulum.     

Formaldehyde at low concentration induces protein tau into globular amyloid-like aggregates in vitro and in vivo

Recent studies have shown that neurodegeneration is closely related to misfolding and aggregation of neuronal tau. Our previous results show that neuronal tau aggregates in formaldehyde solution and that aggregated tau induces apoptosis of SH-SY5Y and hippocampal cells. In the present study, based on atomic force microscopy (AFM) observation, we have found that formaldehyde at low concentrations induces tau polymerization whilst acetaldehyde does not. Neuronal tau misfolds and aggregates into globular-like polymers in 0.01-0.1% formaldehyde solutions. Apart from globular-like aggregation, no fibril-like polymerization was observed when the protein was incubated with formaldehyde for 15 days. SDS-PAGE results also exhibit tau polymerizing in the presence of formaldehyde. Under the same experimental conditions, polymerization of bovine serum albumin (BSA) or alpha-synuclein was not markedly detected. Kinetic study shows that tau significantly misfolds and polymerizes in 60 minutes in 0.1% formaldehyde solution. However, presence of 10% methanol prevents protein tau from polymerization. This suggests that formaldehyde polymerization is involved in tau aggregation. Such aggregation process is probably linked to the tau's special "worm-like" structure, which leaves the epsilon-amino groups of Lys and thiol groups of Cys exposed to the exterior. Such a structure can easily bond to formaldehyde molecules in vitro and in vivo. Polymerizing of formaldehyde itself results in aggregation of protein tau. Immunocytochemistry and thioflavin S staining of both endogenous and exogenous tau in the presence of formaldehyde at low concentrations in the cell culture have shown that formaldehyde can induce tau into amyloid-like aggregates in vivo during apoptosis. The significant protein tau aggregation induced by formaldehyde and the severe toxicity of the aggregated tau to neural cells may suggest that toxicity of methanol and formaldehyde ingestion is related to tau misfolding and aggregation.     

The action of products of the formaldehyde reaction with different amines on nucleic acids and their components

The kinetics and equilibrium of the reaction between nucleic acids components and the products of formaldehyde interaction with ethanolamine and different amino acids has been studied. These parameters were found to be similar for all the products used. The destabilization of the N-glycosidic bond in deoxyadenosine caused by formaldehyde derivatives of different amines was studied. The rate of the cleavage of the N-glycosidic bond under the action of formaldehyde derivatives of glycine and ethanolamine was found to be 10 times greater than that under the action of formaldehyde derivatives of other amines. It is shown that DNA preparations with different content of adenine can be obtained by adding the product of formaldehyde reaction with glycine to DNA.     

Behaviour of DNA-RNase A complex in the presence of formaldehyde]

A formaldehyde-produced fixation of defects caused by a despiralizing action of a protein was studied in the case of DNA-RNAase A complex. The concentration of the defects fixed was measured by kinetic formaldehyde method (KF-method). It was shown that following processes take place in the complex in the presence of formaldehyde: (a) fixation of defects; (b) unwinding of DNA; (c) inactivation of the protein. The rates of all these processes depend on the concentration of formaldehyde, phi. At formaldehyde concentrations above some critical value phic the protein is inactivated before the defects are fixed. At phi less than phic the protein inactivation proceeds more slowly than the fixation of defects; at sufficiently low formaldehyde concentration no inactivation of protein occurs practically during the fixation time (20 min). The number of new defects formed during the time of fixation is linear with the formaldehyde concentration in the region where no inactivation of the protein occurs. Therefore the initial concentration of defects can be determined through an extrapolation to zero concentration of formaldehyde. On the basis of the data obtained a method is proposed for the evaluation of the number of defects in DNA caused by the despiralizing action of proteins. A model is proposed describing the behaviour of the complexes of DNA with despiralizing proteins in the presence of formaldehyde.     

Regulation phenomena in methanol consuming yeasts: An experiment with model discrimination

Assimilation as well as dissimilation of methanol in yeasts takes place through its oxidative intermediate formaldehyde which is several times more toxic to the growth of microorganisms than methanol itself. Still, the role of formaldehyde, produced during methanol assimilation, upon growth of yeasts is not clear. In the present paper, an attempt has been made to throw some light upon this aspect. Starting with a basic frame work for methanol uptake by yeasts, several models were developed assuming different modes of regulation of key enzymes by methanol and/or formaldehyde. The main feature of the basic framework consists in consideration of two routes for oxidation of formaldehyde to CO₂, one associated and the other not associated with production of energy. Further, the rate of energy production form the energy-associated oxidation of formaldehyde is assumed to be controlled by the rate of energy consumption by anabolic reactions. The models were discriminated by subjecting these to biological constraints. As a result, the successful model suggests that in spite of higher inherent toxicity of formaldehyde, methanol exerts the controlling influence upon growth under normal conditions.     

Studies on the mutagenic action of formaldehyde in Drosophila

Summary Drosophila males were exposed to a sublethal concentration of cyanide gas prior to the injection of formaldehyde solutions. Compared to the controls which only received formaldehyde the frequency of sex-linked lethals was increased after the cyanide pretreatment in altogether six independent experiments. These results are taken as further proof that formaldehyde exerts at least part of its mutagenic effects via the formation of peroxides. It is suggested that an excessive amount of hydrogen peroxide, due to inhibition of the cytochrome and catalase enzyme systems, favours the formation of a mutagenic, organic peroxide, presumably dihydroxydimethyl peroxide. The fact that formaldehyde exerts an inhibiting effect on catalase in its own right might be of importance for the interpretation of its mutagenic action.It was also observed that after cyanide pretreatment, the mutagenic effectiveness of a mixture of formaldehyde and hydrogen peroxide was lower than that of formaldehyde alone. These findings can be interpreted by assuming that high concentrations of dihydroxydimethyl peroxide or of a combination of cyanide and this peroxide, eliminate selectively germ cells with induced mutations. It is possible that the same explanation applies to the low mutagenic effectiveness of a mixture of formaldehyde and hydrogen peroxide compared with that of formaldehyde alone when both are preceded by cyanide.With 3 figures in the text     

The effect of formaldehyde containing fixatives on ribonuclease activity

Summary 1. The inactivation of crystalline ribonuclease by formaldehyde and formaldehyde containing fixatives (Serra's solution) is demonstrated.2. The rate of inactivation is shown to be dependent uponph, formaldehyde concentration, and time of action of the fixative.3. The effect of formaldehyde containing fixatives on the RNase activity in sections from fixed tissues is discussed, and the inactivation of that enzyme system in rat pancreas is demonstrated.With 2 Figures in the Text     

Removal efficiency and mechanisms of formaldehyde by five species of plants in air-plant-water system

The foliar uptake and transport rates of formaldehyde as well as the abilities of leaf extracts to breakdown formaldehyde were investigated to discuss the formaldehyde removal efficiency and mechanism by five species of plants from air. Results showed that formaldehyde could be transported from air via leaves and roots to rhizosphere water. When exposed to 0.56 mg·m^?3 formaldehyde, the formaldehyde removal rate ranged from 18.64 to 38.47 μg·h^?1g^?1 FW (fresh weight). According to the mass balance in the air–plant–water system, the main mechanism of the formaldehyde loss was its breakdown in plant tissues caused by both enzymatic reaction and redox reaction. Higher oxidation potentials of the leaf-extracts of Wedelia chinensis and Desmodium motorium corresponded well to higher abilities to breakdown added formaldehyde than other plants. Based on the different abilities of fresh and boiled leaf-extracts to dissipate formaldehyde, the enzymatic reaction in Chenopodium album L. was the dominant mechanism while the redox reaction in Kochia scoparia (L.) Schrad. and Silene conoidea L. was the main formaldehyde breakdown mechanism when exposed to low-level formaldehyde in air. The redox mechanism suggested that the formaldehyde removal may be increased by an increasing level of reactive oxygen species (ROS) induced by the environmental stress.