Inactivation of alcohol and retinol dehydrogenases by acetaldehyde and formaldehyde.

The rapid and progressive inactivation of alcohol dehydrogenase from horse liver, rat liver and from human retina and of retinol dehydrogenase of rat liver by low concentrations of acetaldehyde or formaldehyde is illustrated. The inactivation of alcohol dehydrogenase can be largely prevented and partially reversed with glutathione. These findings are discussed as a model for better understanding of toxic effects of alcohol and in the context of the importance of protein turnover measurements for clarification of untoward alcohol effects.     

Steady-state kinetics of formaldehyde dehydrogenase and formate dehydrogenase from a methanol-utilizing yeast, Candida boidinii.

Initial velocity studies and product inhibition studies were conducted for the forward and reverse reactions of formaldehyde dehydrogenase (formaldehyde: NAD oxidoreductase, EC 1.2.1.1) isolated from a methanol-utilizing yeast Candida boidinii. The data were consistent with an ordered Bi-Bi mechanism for this reaction in which NAD+ is bound first to the enzyme and NADH released last. Kinetic studies indicated that the nucleoside phosphates ATP, ADP and AMP are competitive inhibitors with respect to NAD and noncompetitive inhibitors with respect to S-hydroxymethylglutathione. The inhibitions of the enzyme activity by ATP and ADP are greater at pH 6.0 and 6.5 than at neutral or alkaline pH values. The kinetic studies of formate dehydrogenase (formate:NAD oxidoreductase, EC 1.2.1.2) from the methanol grown C. boidinii suggested also an ordered Bi-Bi mechanism with NAD being the first substrate and NADH the last product. Formate dehydrogenase the last enzyme of the dissimilatory pathway of the methanol metabolism is also inhibited by adenosine phosphates. Since the intracellular concentrations of NADH and ATP are in the range of the Ki values for formaldehyde dehydrogenase and formate dehydrogenase the activities of these main enzymes of the dissimilatory pathway of methanol metabolism in this yeast may be regulated by these compounds.     

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.     

Effects of formaldehyde on mitochondrial dysfunction and apoptosis in SK-N-SH neuroblastoma cells

Methanol ingestion is neurotoxic in humans due to its metabolites, formaldehyde and formic acid. Here, we compared the cytotoxicity of methanol and its metabolites on different types of cells. While methanol and formic acid did not affect the viability of the cells, formaldehyde (200–800 μg/mL) was strongly cytotoxic in all cell types tested. We investigated the effects of formaldehyde on oxidative stress, mitochondrial respiratory functions, and apoptosis on the sensitive neuronal SK-N-SH cells. Oxidative stress was induced after 2 h of formaldehyde exposure. Formaldehyde at a concentration of 400 μg/mL for 12 h of treatment greatly reduced cellular adenosine triphosphate (ATP) levels. Confocal microscopy indicated that the mitochondrial membrane potential (MMP) was dose-dependently reduced by formaldehyde. A marked and dose-dependent inhibition of mitochondrial respiratory enzymes, viz., NADH dehydrogenase (complex I), cytochrome c oxidase (complex IV), and oxidative stress-sensitive aconitase was also detected following treatment with formaldehyde. Furthermore, formaldehyde caused a concentration-dependent increase in nuclear fragmentation and in the activities of the apoptosis-initiator caspase-9 and apoptosis-effector caspase-3/-7, indicating apoptosis progression. Our data suggests that formaldehyde exerts strong cytotoxicity, at least in part, by inducing oxidative stress, mitochondrial dysfunction, and eventually apoptosis. Changes in mitochondrial respiratory function and oxidative stress by formaldehyde may therefore be critical in methanol-induced toxicity.     

Regulation of protein synthesis in methylotrophic yeasts: Repression of methanol dissimilating enzymes by nitrogen limitation

The influence of nitrogen limitation on the regulation of the methanol oxidizing enzymes alcohol oxidase, catalase, formaldehyde dehydrogenase and formate dehydrogenase in the two methylotrophic yeastsHansenula polymorpha andKloeckera sp. 2201 was studied in continuous culture. When shifted from carbon-limited growth conditions (with a mixture of glucose and methanol as carbon sources) to a nitrogen-limited environment both cultures were found to go through a transition phase where neither enhanced residual concentrations of the nitrogen source nor of one of the two carbon sources could be detected in the supernatant. As soon as nitrogen became a limiting substrate an immediate reorganisation of the cell composition was initiated: protein content of the cells dropped to approximately 40% of its initial value, glycogen was synthesized and the enzyme composition of the cells was changed. The peroxisomal enzymes alcohol oxidase and catalase in both organisms and the two dehydrogenases for formaldehyde and formate in cells ofKloeckera sp. 2201 were subject to degradation (catabolite inactivation). The measured rates of inactivation indicated that in cells ofH. polymorpha this process might be limited to peroxisomes, whereas inKloeckera sp. 2201 the degradation was found to affect peroxisomal as well as cytoplasmic enzymes. In contrast to methanol dissimilating enzymes the net rate of synthesis of hexokinase, glucose-6-phosphate dehydrogenase and 6-phosphogluconate dehydrogenase was not affected by this process but those enzymes were synthesized with increased rates.     

Effect of formaldehyde on growth of obligate methylotroph Methylobacillus flagellatum in a substrate non-limited continuous culture

The ribulose monophosphate cycle methylotroph Methylobacillus flagellatum was grown under oxyturbidostat conditions on mixtures of methanol and formaldehyde. Formaldehyde when added at low concentration (50 mg/l) increased the methanol consumption and the yield of biomass. The presence of 150–300 mg/l of formaldehyde resulted in an increase of the growth rate from 0.74 to about 0.79–0.82 h^-1. The presence of 500 mg/l of formaldehyde in the inflow decreased culture growth characteristics. Activities of methanol dehydrogenase and enzymes participating in formaldehyde oxidation and assimilation were measured. The enzymological profiles obtained are discussed.Abbreviations MDH methanol dehydrogenase - NAD-linked FDDH NAD-linked formaldehyde dehydrogenase - DLFDDH dye-linked formaldehyde dehydrogenase - DLFDH dye-linked formate dehydrogenase - GPDH glucose-6-phosphate dehydrogenase - PGDH 6-phosphogluconate dehydrogenase - RuMP cycle ribulose monophosphate cycle     

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.     

Purification of formaldehyde and formate dehydrogenases from pea seeds by affinity chromatography and S-formylglutathione as the intermediate of formaldehyde metabolism

Formaldehyde dehydrogenase (EC 1.2.1.1) and formate dehydrogenase (EC 1.2.1.2) have been isolated in pure form from pea seeds by a rapid procedure which employs column chromatographies on 5′-AMP-Sepharose, Sephacryl S-200, and DE32 cellulose. The apparent molecular weights of formaldehyde and formate dehydrogenases are, respectively, 82,300 and 80,300 by gel chromatography, and they both consist of two similar subunits. The isoelectric point of formaldehyde dehydrogenase is 5.8 and that of formate dehydrogenase is 6.2. The purified formate dehydrogenase gave three corresponding protein and activity bands in electrophoresis and isoelectric focusing on polyacrylamide gel whereas formaldehyde dehydrogenase gave only one band. Formaldehyde dehydrogenase catalyzes the formation of S-formylglutathione from formaldehyde, and glutathione. Formate dehydrogenase can, besides formate, also use S-formylglutathione and two other formate esters as substrates. S-Formylglutathione has a lower K_m value (0.45 mm) than formate (2.1 mm) but the maximum velocity of S-formylglutathione is only 5.5% of that of formate. Pea extracts also contain a highly active S-formylglutathione hydrolase which has been separated from glyoxalase II (EC 3.1.2.6) and partially purified. S-Formylglutathione hydrolase is apparently needed between formaldehyde and formate dehydrogenases in the metabolism of formaldehyde in pea seeds, in contrast to what was recently reported for Hansenula polymorpha, a yeast grown on methanol.     

Inhibition of the low-Km mitochondrial aldehyde dehydrogenase by diethyl maleate and phorone in vivo and in vitro. Implications for formaldehyde metabolism.

Formaldehyde can be oxidized primarily by two different enzymes, the low-Km mitochondrial aldehyde dehydrogenase and the cytosolic GSH-dependent formaldehyde dehydrogenase. Experiments were carried out to evaluate the effects of diethyl maleate or phorone, agents that deplete GSH from the liver, on the oxidation of formaldehyde. The addition of diethyl maleate or phorone to intact mitochondria or to disrupted mitochondrial fractions produced inhibition of formaldehyde oxidation. The kinetics of inhibition of the low-Km mitochondrial aldehyde dehydrogenase were mixed. Mitochondria isolated from rats treated in vivo with diethyl maleate or phorone had a decreased capacity to oxidize either formaldehyde or acetaldehyde. The activity of the low-Km, but not the high-Km, mitochondrial aldehyde dehydrogenase was also inhibited. The production of CO2 plus formate from 0.2 mM-[14C]formaldehyde by isolated hepatocytes was only slightly inhibited (15-30%) by incubation with diethyl maleate or addition of cyanamide, suggesting oxidation primarily via formaldehyde dehydrogenase. However, the production of CO2 plus formate was increased 2.5-fold when the concentration of [14C]formaldehyde was raised to 1 mM. This increase in product formation at higher formaldehyde concentrations was much more sensitive to inhibition by diethyl maleate or cyanamide, suggesting an important contribution by mitochondrial aldehyde dehydrogenase. Thus diethyl maleate and phorone, besides depleting GSH, can also serve as effective inhibitors in vivo or in vitro of the low-Km mitochondrial aldehyde dehydrogenase. Inhibition of formaldehyde oxidation by these agents could be due to impairment of both enzyme systems known to be capable of oxidizing formaldehyde. It would appear that a critical amount of GSH, e.g. 90%, must be depleted before the activity of formaldehyde dehydrogenase becomes impaired.     

Potential biological indicators for glutaraldehyde and formaldehyde sterilization processes

The present study aimed to isolate, select, and evaluate bacterial isolates with potential for use as biological indicators for sterilization with glutaraldehyde and/or formaldehyde. A total of 340 local Bacillus isolates were screened for glutaraldehyde and/or formaldehyde resistance by determination of minimum inhibitory concentrations (MICs), minimum bactericidal concentrations (MBCs), and extinction time and were compared with B. subtilis (var. niger) ATCC 9372, the biological indicator for ethylene oxide sterilization, as reference. Of these, 85 isolates had glutaraldehyde MICs of 0.5% or higher, while 29 had formaldehyde MICs of 0.04% or higher. Of the 29 resistant isolates, 15 had MBCs of 0.05% or more. Extinction times were used to evaluate the bactericidal/sporicidal activity of glutaraldehyde. Eight had inactivation times of more than 5 h in 2% glutaraldehyde (pH 8), whereas 12 had inactivation times of more than 3 h in l% formaldehyde, with one isolate in common. These 19 isolates were selected and evaluated as potential biological indicators for aldehydes by determination of the decimal reduction times (D values), compared with the reference strain. Eight glutaraldehyde-resistant isolates exhibited D values 2.0- to 3.5-fold higher than the reference strain (30 min.). Only five of 12 formaldehyde resistant isolates had D values higher than that of the reference strain. Using six resistant isolates, temperature coefficient values between 2.11 and 3.02 were obtained for 2% formaldehyde. Finally, 14 isolates were tested for potential pathogenicity and were identified to species level. All of the eight glutaraldehyde-resistant isolates, including the isolate with dual resistance, and three formaldehyde-resistant isolates were B. licheniformis, while two other formaldehyde-resistant isolates were B. cereus. Six of the selected B. licheniformis isolates are potential biological indicators for sterilization processes using aldehydes. Three can be suggested for glutaraldehyde only and three for both aldehydes. Electronic Publication     

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.     

Cytotoxic effects of methanol, formaldehyde, and formate on dissociated rat thymocytes: A possibility of aspartame toxicity

Aspartame is a widely used artificial sweetener added to many soft beverages and its usage is increasing in health-conscious societies. Upon ingestion, this artificial sweetener produces methanol as a metabolite. In order to examine the possibility of aspartame toxicity, the effects of methanol and its metabolites (formaldehyde and formate) on dissociated rat thymocytes were studied by flow cytometry. While methanol and formate did not affect cell viability in the physiological pH range, formaldehyde at 1–3 mmol/L started to induce cell death. Further increase in formaldehyde concentration produced a dose-dependent decrease in cell viability. Formaldehyde at 1 mmol/L or more greatly reduced cellular content of glutathione, possibly increasing cell vulnerability to oxidative stress. Furthermore, formaldehyde at 3 mmol/L or more significantly increased intracellular concentration of Ca²⁺([Ca²⁺]_i) in a dose-dependent manner. Threshold concentrations of formaldehyde, a metabolite of methanol, that affected the [Ca²⁺]_iand cellular glutathione content were slightly higher than the blood concentrations of methanol previously reported in subjects administered abuse doses of aspartame. It is suggested that aspartame at abuse doses is harmless to humans. This revised version was published online in August 2006 with corrections to the Cover Date.     

Cofactor-dependent pathways of formaldehyde oxidation in methylotrophic bacteria

Methylotrophic bacteria can grow on a number of substrates as energy source with only one carbon atom, such as methanol, methane, methylamine, and dichloromethane. These compounds are metabolized via the cytotoxin formaldehyde. The formaldehyde consumption pathways, especially the pathways for the oxidation of formaldehyde to CO(2) for energy metabolism, are a central and critical part of the metabolism of these aerobic bacteria. Principally, two main types of pathways for the conversion of formaldehyde to CO(2) have been described: (1) a cyclic pathway initiated by the condensation of formaldehyde with ribulose monophosphate, and (2) distinct linear pathways that involve a dye-linked formaldehyde dehydrogenase or C(1) unit conversion bound to the cofactors tetrahydrofolate (H(4)F), tetrahydromethanopterin (H(4)MPT), glutathione (GSH), or mycothiol (MySH). The pathways involving the four cofactors have in common the following sequence of events: the spontaneous or enzyme-catalyzed condensation of formaldehyde and the respective C(1) carrier, the oxidation of the cofactor-bound C(1) unit and its conversion to formate, and the oxidation of formate to CO(2). However, the H(4)MPT pathway is more complex and involves intermediates that were previously known solely from the energy metabolism of methanogenic archaea. The occurrence of the different formaldehyde oxidation pathways is not uniform among different methylotrophic bacteria. The pathways are in part also used by other organisms to provide C(1) units for biosynthetic reactions (e.g., H(4)F-dependent enzymes) or detoxification of formaldehyde (e.g., GSH-dependent enzymes).     

On-line detection of atmospheric formaldehyde by a conductometric biosensor

Atmospheric formaldehyde (CH(2)O) was detected under continuous flow conditions by an on-line system comprising of a wet scrubber for a continuous transfer of the pollutant to an aqueous solution, a micro-reactor containing immobilized formaldehyde dehydrogenase (FDH) and a conductometric transducer. By this system atmospheric formaldehyde concentrations in the range 0.05-2 ppm were detected with a sensitivity of 20 microS/ppm. In this concentration range the immobilized enzyme oxidized all the sampled formaldehyde molecules to formic acid, avoiding cumbersome calibration procedures. The operational stability of the biosensor was at least 3 months, working continuously 10 h/day at room temperature.     

Two-component system that regulates methanol and formaldehyde oxidation in Paracoccus denitrificans

A chromosomal region encoding a two-component regulatory system, FlhRS, has been isolated from Paracoccus denitrificans. FlhRS-deficient mutants were unable to grow on methanol, methylamine, or choline as the carbon and energy source. Expression of the gene encoding glutathione-dependent formaldehyde dehydrogenase (fhlA) was undetectable in the mutant, and expression of the S-formylglutathione hydrolase gene (fghA) was reduced in the mutant background. In addition, methanol dehydrogenase was immunologically undetectable in cell extracts of FhlRS mutants. These results indicate that the FlhRS sensor-regulator pair is involved in the regulation of formaldehyde, methanol, and methylamine oxidation. The effect that the FlhRS proteins exert on the regulation of C₁ metabolism might be essential to maintain the internal concentration of formaldehyde below toxic levels.     

Inhibition of the oxidation of acetaldehyde and formaldehyde by hepatocytes and mitochondria by crotonaldehyde

Crotonaldehyde was oxidized by disrupted rat liver mitochondrial fractions or by intact mitochondria at rates that were only 10 to 15% that of acetaldehyde. Although a poor substrate for oxidation, crotonaldehyde is an effective inhibitor of the oxidation of acetaldehyde by mitochondrial aldehyde dehydrogenase, by intact mitochondria, and by isolated hepatocytes. Inhibition by crotonaldehyde was competitive with respect to acetaldehyde, and the Ki for crotonaldehyde was about 5 to 20 microM. Crotonaldehyde had no effect on the oxidation of glutamate or succinate. Very low levels of acetaldehyde were detected during the metabolism of ethanol. Crotonaldehyde increased the accumulation of acetaldehyde more than 10-fold, indicating that crotonaldehyde, besides inhibiting the oxidation of added acetaldehyde, also inhibited the oxidation of acetaldehyde generated by the metabolism of ethanol. Formaldehyde was a substrate for the low-Km mitochondrial aldehyde dehydrogenase, as well as for a cytosolic, glutathione-dependent formaldehyde dehydrogenase. Crotonaldehyde was a potent inhibitor of mitochondrial oxidation of formaldehyde, but had no effect on the activity of formaldehyde dehydrogenase. In hepatocytes, crotonaldehyde produced about 30 to 40% inhibition of formaldehyde oxidation, which was similar to the inhibition produced by cyanamide. This suggested that part of the formaldehyde oxidation occurred via the mitochondrial aldehyde dehydrogenase, and part via formaldehyde dehydrogenase. The fact that inhibition by crotonaldehyde is competitive may be of value since other commonly used inhibitors of aldehyde dehydrogenase are irreversible inhibitors of the enzyme.     

Activities of the enzymes of formaldehyde catabolism in recombinant strains of <Emphasis Type="Italic">Hansenula polymorpha</Emphasis>

Activities of the enzymes of formaldehyde (FA) catabolism in recombinant strains of the methylotrophic yeast Hansenula polymorpha overproducing NAD⁺- and glutathione-dependent formaldehyde dehydrogenase (FADH) were studied under different cultivation conditions and at elevated FA content. Southern dot-blot analysis confirmed the presence of six to eight copies of the target FLD1 gene in stable recombinant clones of H. polymorpha. Under certain cultivation conditions, the transformants resistant to elevated FA concentrations were shown to produce FADH and other bioanalytically important enzymes: formate dehydrogenase, alcohol dehydrogenase, alcohol oxidase, and formaldehyde reductase. The optimal cultivation conditions for recombinants were determined, resulting in maximum synthesis of FADH: methanol as a carbon source, methylamine as a nitrogen source, FA as an inducer, temperature of 37°C, and cells in the early exponential phase of growth.     

Purification and properties of an NAD(P)+-linked formaldehyde dehydrogenase from Methylococcus capsulatus (Bath).

Crude soluble extracts of Methylococcus capsulatus strain Bath, grown on methane, were found to contain NAD(P)+-linked formaldehyde dehydrogenase activity. Activity in the extract was lost on dialysis against phosphate buffer, but could be restored by supplementing with inactive, heat-treated extract (70 degrees C for 12 min). The non-dialysable, heat-sensitive component was isolated and purified, and has a molecular weight of about 115000. Sodium dodecyl sulphate gel electrophoresis of the protein suggested there were two equal subunits with molecular weights of 57000. The heat-stable fraction, which was necessary for activity of the heat-sensitive protein, was trypsin-sensitive and presumed to be a low molecular weight protein or peptide. A number of thiol compounds and other common cofactors could not replace the component present in the heat-treated soluble extract. The purified formaldehyde dehydrogenase oxidized three other aldehydes with the following Km values: 0.68 mM (formaldehyde); 0.075 mM (glyoxal); 7.0 mM (glycolaldehyde); and 2.0 mM (DL-glyceraldehyde). NAD+ or NADP+ was required for activity, with Km values of 0.063 and 0.155 mM respectively, and could not be replaced by any of the artificial electron acceptors tested. The enzyme was heat-stable at 45 degrees C for at least 10 min and had temperature and pH optima of 45 degrees C and pH 7.2 respectively. A number of metal-binding agents and substrate analogues were not inhibitory. Thiol reagents gave varying degrees of inhibition, the most potent being p-hydroxymercuribenzoate which at 1 mM gave 100% inhibition. The importance of possessing an NAD(P)+-linked formaldehyde dehydrogenase, with respect to M. capsulatus, is discussed.     

Enhanced formaldehyde detoxification by overexpression of glutathione-dependent formaldehyde dehydrogenase from Arabidopsis

The ADH2 gene codes for the Arabidopsis glutathione-dependent formaldehyde dehydrogenase (FALDH), an enzyme involved in formaldehyde metabolism in eukaryotes. In the present work, we have investigated the potential role of FALDH in detoxification of exogenous formaldehyde. We have generated a yeast (Saccharomyces cerevisiae) mutant strain (sfa1Delta) by in vivo deletion of the SFA1 gene that codes for the endogenous FALDH. Overexpression of Arabidopsis FALDH in this mutant confers high resistance to formaldehyde added exogenously, which demonstrates the functional conservation of the enzyme through evolution and supports its essential role in formaldehyde metabolism. To investigate the role of the enzyme in plants, we have generated Arabidopsis transgenic lines with modified levels of FALDH. Plants overexpressing the enzyme show a 25% increase in their efficiency to take up exogenous formaldehyde, whereas plants with reduced levels of FALDH (due to either a cosuppression phenotype or to the expression of an antisense construct) show a marked slower rate and reduced ability for formaldehyde detoxification as compared with the wild-type Arabidopsis. These results show that the capacity to take up and detoxify high concentrations of formaldehyde is proportionally related to the FALDH activity in the plant, revealing the essential role of this enzyme in formaldehyde detoxification.     

Inhalation of formaldehyde does not induce genotoxic effects in broncho-alveolar lavage (BAL) cells of rats

Male Fischer-344 rats were exposed to formaldehyde (FA) by inhalation for 4 weeks (6 h/day, 5 days/week). Groups of six rats each were exposed to the target concentrations of 0, 0.5, 1, 2, 6, 10 and 15 ppm. Potential genotoxic effects in the lung were investigated as part of a comprehensive study on local and systemic toxic and genotoxic effects. Broncho-alveolar lavage (BAL) cells were obtained by lung lavage with physiological saline and counted. From one half of the cells, slides for the micronucleus test (MNT) were prepared by cytocentrifugation; with the other half, the comet assay was performed. DNA migration in the comet assay was measured both directly and after irradiation of the cells with 2 Gy gamma-radiation. The latter modification of the comet assay was included to increase its sensitivity for the detection of DNA-protein cross-links (DPX). For the comet assay, four slides were analysed from each cell sample, two without and two with irradiation. From each slide, 50 randomly selected cells were measured by image analysis and tail intensity (% tail DNA) and tail moment were evaluated. The frequency of micronucleated BAL cells was determined in acridine orange-stained slides by analysing 2000 cells per animal. FA did not induce any significant effect in any of the genotoxicity tests performed. It can be concluded that inhalation of FA in a 28 days study with FA concentrations up to 15 ppm does not lead to genotoxic effects in BAL cells of rats. Because detection of DPX by the comet assay is a very sensitive biomarker of FA exposure of cells, our results suggest that there is no genetically relevant exposure of the lung after FA inhalation. The results of our inhalation study, which was performed under GLP conditions, call into question the biological significance of previously reported genotoxic effects in the lung of rats after FA inhalation.