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[Effect of formaldehyde on energy metabolism in postnatal rat cortex neurons in culture].

OBJECTIVE: The mechanism of the effect of formaldehyde on CNS which is much concerned to formaldehyde poisoning was studied. METHODS: In the present study, incubation of postnatal rat cortex neurons in culture with formaldehyde at 1, 2, 4, 8 mg/L (medium) was carried out to evaluate the effect of formaldehyde on energy metabolism. RESULTS: The result of cytochemistry showed a significant down-regulation of cytochrome oxidase activity after consecutive formaldehyde treatment for 4 hours compared with the control (P < 0.01), the significant dosage-response relationship was also observed (R value is - 0.92, P < 0.01). CONCLUSION: The result demonstrates that excessive exposure of formaldehyde can decrease cytochrome oxidase activity in cortex neurons which indicates energy metabolism will be decreased and therefore normal physiology function would be damaged.

Animals↗

[Stable carbon isotope analysis method for the atmospheric formaldehyde].

A method of compound-specific stable carbon isotopic analysis for the research about the sources of atmospheric formaldehyde was preliminary studied using gas chromatography/combustion/isotope ratio mass spectrometry (GC/C/IRMS) via 2, 4-dinitrophenylhydrazine (DNPH) derivatization. In order to evaluate the reproducibility, the accuracy and the carbon isotope effects of the method, formaldehyde with different delta 13C values were used to simulate the sampling procedure. The results show that the maximal analytical deviation for all formaldehyde 2, 4-dinitrophenylhydrazone is 0.3 per thousand and the average deviations between the determined and theoretical delta 13C values of them are 0.24 per thousand +/- 0.14per thousand (ranged from 0.03 per thousand to 0.35 per thousand), less than 0.5 per thousand the technical specifications of the GC/C/IRMS system. These mean that no carbon isotopic fractionation occurred during the procedure. The study for the indoor and outdoor atmospheric formaldehyde in the restaurant show that the stable carbon isotopic compositions are significant different for different sources of formaldehyde. The present method could provide valuable information about the sources of atmospheric formaldehyde.

Air Pollutants↗

[Occupational exposure to formaldehyde in three pathology departments].

Although formaldehyde has recently been classified by the IARC as "carcinogenic in humans" (class 1), it is still widely used in pathology departments for the fixing and conservation of biological tissues. Its use therefore raises the question of occupational exposure. The present paper reports the results of an environmental monitoring campaign to evaluate pollution by formaldehyde in various areas of three pathology departments. Chemi-adsorbent cartridges able to adsorb airborne formaldehyde were used to detect the substance. Quantitative determination of the formaldehyde was carried out by means of liquid chromatography (HPLC). The concentrations of airborne formaldehyde in the areas monitored were fairly modest, being below the limits of indoor concentration proposed by the OSHA. In one of the three departments, however these limits were exceeded in 40% of the samples taken in the room used for the storage of containers. As yet, in spite of the recent class 1 classification by the IARC, no provisions have been made to ban the use of formaldehyde. It is therefore essential to draw up environmental monitoring programmes in order to evaluate occupational exposure and to assess the efficacy of any preventive measures adopted.

Air Pollution, Indoor↗

[Environmental monitoring and biological monitoring of young people exposed to nonoccupational levels of formaldehyde, toluene and other hydrocarbons].

During the period of 1983-1985, in two of apprentice schools of P. town the health disorders were investigated in the total of 82 apprentices 15-18 years old from the environment with elevated concentrations of formaldehyde and toluene. The study was contrasted with a control total of 42 apprentices. Cytogenetical examination has been performed, and selected immunological parameters in both blood serum and saliva have been assessed with red and white blood cells counts including differential formula of white blood cells. In addition, the atmospheric toxicity of formaldehyde and vapours of organic solvents (toluene, xylene, varnish naphtha) was measured. A single biological exposure test has been performed for the detection toluene. Statistically significant were differences in occurrence of cell chromosomal aberrations between the group of long term formaldehyde and toluene exposure (averagely 3.53% ABB) and controls (2.21% ABB) as obtained in 1983 and 1984, and so were differences between the long term-to-toluene exposed group (3.30% ABB) and the above mentioned control group as obtained in 1984. No similar results were stated between the long term-to-formaldehyde exposed (3.07% ABB) and control (2.55% ABB) groups in 1985. The main evidence consisted in finding the genotoxical/clastogenic effect of observed agents associated with mainly chromosomal abnormalities of chromatide type. It outflowed from the determination of selected serum proteins (Ig and acute phase proteins) and salivary lysozyme that the group under the combined influence of formaldehyde and toluene showed significantly lower IgG and higher alpha-1-antitrypsin (A1AT). The group at risk of toluene was characteristical in elevated concentrations of alpha-2-macroglobulin (A2M) and A1AT. Most pronounced changes in first year had been revealed through the evaluation of the influence of the duration at risk (significant decrease in IgA and prealbumin, and the increase in A2M and A1AT). The infectious disease as experienced 2 month prior the collection resulted in a significant decrease of IgM, A2M and A1AT in risky groups in individuals with infection in anamnesis. Salivary lysozyme concentration of apprentice environmentally exposed to formaldehyde in the noon showed the decrease, whereas its increase occurred in controls with the difference on 5% significancy level. Blood count assessements showed no significant differences between the investigated values as well as any were assessed between the incidence of health disorders of apprentices and their correspondance to the given group.

Adolescent↗

[Detection of the presence of formaldehyde in textiles by using color tests with acetylacetone and chromotropic acid].

In 61 textile materials of cotton, wool and synthetic fibre formaldehyde was determined using colour tests with acetylacetone and chromotropic acid. Full agreement of the results of both tests was demonstrated. In 61 studied materials formaldehyde was demonstrated in 44 samples and in 17 samples it was absent. Formaldehyde was present in materials submitted to end-use finish. The possibility was showed also of formaldehyde passage from the finished materials into materials not containing it following their storage together. Frequent washing and ironing of materials after finish may lead to formaldehyde loss from the materials. The usefulness is stressed of colour tests for the diagnosis and prevention of formaldehyde-induced clothing-related eczema.

Color↗

[Analysis of formaldehyde in various chemical products for household use and in shampoos and bath liquids].

In the years 1987-1988 in cooperation with 34 Province Sanitary-Epidemiological Stations 938 samples of shampoos and bathing fluids were investigated, among them 40 imported shampoos, besides that 829 samples of chemical products for household use were analysed for the presence of formaldehyde. In the products which should not contain formaldehyde this compound was found in amounts from 0 to 50 mg/kg in 84.75% of shampoos and bathing fluids (77.18% of the samples contained no formaldehyde), 87.03% of fluids for washing of vessels, rinsing and softening of fabrics, and for washing or refrigerators (in 75.13% of these products formaldehyde was not found). The authors suggest that the permissible formaldehyde level for these products should be 50 mg/kg and should be accepted as contamination. In these products in which the permitted formaldehyde level was 0.1% already 99.12% of the samples was below that value.

Baths↗

Effects of formaldehyde on the isolated phrenic nerve and the phrenic nerve-diaphragm preparation of the rat, in vitro.

Formaldehyde, 0.5-4.5 mM, increased the threshold for electrical excitation of the nerve, and led to a partial and reversible inhibition of the compound action potential (cAP). The depression was not enhanced by high frequency stimulation. At 8.9 mM or higher, the depression of the nerve excitability could not be reversed. The inhibition of the nerve developed more slowly than that of the muscle, and the nerve was unaffected after 10 min exposure to 2.2 mM. Formaldehyde, 2.2 mM, caused an immediate depression of the indirectly (through the nerve) and directory (at the muscle) elicited twitch tension. After 10 min the tensions were reduced to respectively, 56% and 49% of control. However, the electromyogram was not changed, indicating that the effect was localized to the excitation-contraction coupling. Tetanic tension (100 Hz in 5 sec) was inhibited more than twitch tension during indirect stimulation, whereas the opposite was found during direct stimulation of the muscle. Thus, during high frequency stimulation, formaldehyde must have an additional effect on the neuromuscular transmission. This effect was localized presynaptically since a fall out of endplate potentials was observed in the formaldehyde-treated diaphragm. In 6.7 mM or higher concentrations the directly or indirectly induced contractions were irreversibly blocked. The resting membrane potential of the muscle cells was unchanged after exposure to formaldehyde. Formaldehyde caused myotonia-like contractions of the diaphragm, occasionally after exposure to low concentrations (2.2 mM), and always after exposure to higher concentrations.(ABSTRACT TRUNCATED AT 250 WORDS)

Action Potentials↗

The Massachusetts program for reducing the risk of formaldehyde exposure.

Urea formaldehyde foam insulation in homes has caused increasing concerns about the adverse health effects associated with residential exposure to formaldehyde emissions. These health effects cover a broad spectrum of symptoms, including neurophysiological effects, respiratory irritations, and eye and skin irritations. Recent studies have also suggested a possible correlation between exposure to formaldehyde vapors and cancer. In 1979, following hundreds of complaints of adverse health effects from occupants of dwellings insulated with urea formaldehyde foam insulation (UFFI), the Massachusetts Department of Public Health issued regulations banning the new installation of UFFI in Massachusetts. New State legislation was adopted in 1986 which reformulated UFFI policy. The law established a minimum concentration of formaldehyde of 0.1 parts per million (ppm) below which removal of the insulation is not required or encouraged. A trust fund financed by industry was established to pay for air testing and for the removal of UFFI from homes if the formaldehyde level exceeds the statutory minimum of 0.1 ppm or if an occupant experiences adverse health effects attributable to the insulation. Based on the Massachusetts experience, these requirements have been identified: the need for flexibility and midcourse corrections in the development of health policy to allow for the incorporation of new scientific information or changes in the economic or political environment, the need for close coordination with all affected parties, and the need for scientific and technical policy development to be joined with economic and political perspectives to ensure smooth implementation of health policies.

Construction Materials↗

[Formaldehyde resistance to gram-negative aerobic rods from municipal sewage water].

In a municipal sewage works, a total of 30 sewage samples (19 from the inlet and 11 from the outlet of the sewage works) were analyzed for the quantitative and orientative qualitative content of microorganisms. With an incidence peak of the total bacterial count of greater than or equal to 1 X 10(6) cfu/ml in the inlet, both samples showed bacterial contents of 1 to 9 X 10(5) cfu/ml with use of MC agar and Endo agar. Fuchsin glistening colonies as well as the total bacterial counts on Sabouraud agar and Leifson agar as well as on kanamycin-esculin agar showed frequency peaks which were one power of ten lower. For pathogenic staphylococci, a distribution below the limit of detection (down to 9 X 10(3) cfu/ml) was found, and in a single case in the region of 10(4) cfu/ml. As a rule, the samples drawn from the outlet of the municipal sewage works showed values which were one power of ten lower than in the inlet. With admixture of formaldehyde in bacteriostatically active concentrations, colonies could still be cultured to a small extent with a final concentration of 0.03 weight % HCHO in the inlet, whereas values were below the limit of detection in all outlet samples. The differentiated Gram-negative aerobic rods were mainly representatives of the species Pseudomonas aeruginosa and Pseudomonas putida. In a modified quantitative suspension trial, only occasional Gram-negative rods in the inlet samples survived 30 min exposure to 0.5 weight % HCHO. In comparison, the results of the outlet samples showed a very much lower resistance to formaldehyde. The 11 strains isolated under these conditions could be classified under six species, including four Pseudomonas aeruginosa strains. Gram-negative rods which had previously tolerated a concentration of 0.12 weight % formaldehyde in the bacteriostasis revealed a raised resistance to formaldehyde only to an inappreciable extent under the conditions of the qualitative suspension trial. Overall, enhancements of resistance to formaldehyde such as we observed in isolates from hospital sewage could not be detected in bacterial strains isolated from the inlet or outlet of a municipal sewage works. The investigations carried out thus do not indicate that a quantitatively significant increase or a persistence of the resistance to formaldehyde is to be expected outside the actual hospital environment.

Drug Resistance, Microbial↗

[Effect of formaldehyde on the ribonucleoprotein structure of Sendai virus].

The effect of formaldehyde on the conformation of Sendai virus ribonucleoprotein (RNP) was studied by electron microscopy and a spectrophotometric method. The effect of formaldehyde on RNP conformation was found to depend strongly on the ionic strength of the solution. Under conditions of a low ionic strength in the presence of 1.5% formaldehyde the tightly coiled rods of RNP stained with uranyl acetate become loosely coiled or almost completely extended. At the same time, formaldehyde reaction with RNP results in a decrease in extinction of the RNP suspension in the 250 to 290 spectral region. However, RNP incubation with formaldehyde in the presence of 0.5M NaCl caused no changes in the morphology and spectral properties of the RNP under study. The results indicate that formaldehyde cannot be used for fixation of Sendai virus nucleocapsids before negative staining for electron microscopy examinations.

Formaldehyde↗

Formaldehyde generation from methenamine salts in spinal cord injury.

To achieve effective suppression of bacteriuria in spinal cord injured (SCI) patients, methenamine mandelate and methenamine hippurate are commonly given with ascorbic acid. Since the effectiveness of ascorbic acid as a urinary acidifier has been challenged and as it also has been suggested that methenamine salts do not produce effective urine formaldehyde concentrations in patients with indwelling urethral catheters, we studied two groups of SCI patients to determine (1) the effect of ascorbic acid on urine pH and formaldehyde concentration when administered with methenamine salts; (2) the effect of an indwelling urethral catheter versus intermittent catheterization on formaldehyde concentration in the urine of SCI patients taking methenamine salts; and (3) the relative urine formaldehyde concentrations produced by treatment with methenamine mandelate and methenamine hippurate in SCI patients. Methenamine mandelate produced significantly higher urine formaldehyde concentrations than did methenamine hippurate, especially among patients with intermittent catheterization. Ascorbic acid produced a significant effect on urine pH but not on formaldehyde concentration.

Anti-Infective Agents, Urinary↗

[Induction by formaldehyde of conformational changes from helix to globule in the myoglobin molecule].

The secondary structure of myoglobin, treated with formaldehyde, has been studied by absorption spectroscopy, circular dichroism and gel-chromatography. The chemical modification of protein leads to disturbance of the polypeptide alpha-helix and destruction of the heme environment. The unfolding of protein in the presence of formaldehyde is a reversible process, the rate of transition is conditioned by temperature and formaldehyde concentration. At certain temperature conditions and formaldehyde concentration it is possible to obtain completely unfolded protein. The denaturation of myoglobin in the presence of formaldehyde is not cooperative in contrast to classical denaturation by pH, temperature, urea and other agents. Presence of some aminoacids causes inhibition of conformational changes in the protein molecule. Possible mechanisms of denaturation of myoglobin in the presence of formaldehyde are discussed.

Circular Dichroism↗

Effect of formaldehyde exposure in the hatcher and of ventilation in confinement facilities on broiler performance.

Broiler embryos and chicks were exposed to formaldehyde vapors (up to 130 ppm) during the final 3 days of incubation. Bacterial load was significantly lower in a formaldehyde-fumigated hatcher than in an unfumigated hatcher. Hatchability was not affected. To determine if exposure to formaldehyde vapors in the hatcher would affect broilers' ability to tolerate variations in air quality, chicks were placed in either adequately or poorly ventilated confinement facilities for 45 days. Total and respirable dust particles (< or = 5 microns in diameter) increased to a greater extent between 5 and 6 weeks of broiler age in the poorly ventilated facility than in the facility with adequate ventilation. Mortality at 6 weeks of age was significantly higher in broilers exposed to formaldehyde in the hatcher and housed with poor ventilation than in broilers exposed to formaldehyde and raised with adequate ventilation. Six-week body weight, feed conversion, and septicemia/toxemia condemnations were adversely affected by poor ventilation. This study found that the quality of air in the confinement facility had a greater influence on broiler productivity than did exposure to formaldehyde vapors in the hatcher.

Aerosols↗

[Nasal patency patterns observed during working hours in a group of technicians habitually exposed to formaldehyde].

Formaldehyde is a substance which is widely used in several work fields, including many medical and biological sectors. It appears that formaldehyde exposure may cause bronchial asthma. Little information is available, however, with regard to upper aereal tracts. The nose is a target organ of major importance for a large range of professional and extra-professional environmental pollutants. In particular, cases of professional rhinitis brought about by exposure to disinfectants have been reported in Literature. In the light of general knowledge related to the close correlation between upper and lower airways, and to the lack of information concerning the effects of short-term formaldehyde exposure on the upper aereal tract, the Authors decided that investigation of such exposure might prove interesting as well as worthwhile. A group of fifteen technicians who work in three different pathology departments and who had been exposed to formaldehyde for at least one year were studied. The purpose of the study was to assess possible alteration in nasal resistances at the end of a normal work shift. The subjects under study were observed according to a procedure which included several clinical, allergological, serological and functional evaluations carried out on specific days of the week. A control group, consisting of eight asymptomatic, non-atopic subjects who had never been exposed to inhalation of irritants was also monitored in the same way. Conclusions were drawn after considering some important variables such as exposure time, possible anatomical alterations of the nose, the presence of respiratory allergies and smoking habits. It was apparent that professional formaldehyde exposure typical of that experienced by technicians working in pathology departments induced a short-term irritant effect on the upper aereal tract, which, even though subclinical, is revealed by a statistically significant increase in nasal resistance. This effect seems to be favoured (at statistically not significant levels) by atopy, cigarette smoking and anatomical alterations of the nose. Our data seem to exclude a chronic cumulative effect of formaldehyde exposure.

Adult↗

A recommended occupational exposure limit for formaldehyde based on irritation.

In recent years, several regulatory agencies and professional societies have recommended an occupational exposure limit (OEL) for formaldehyde. This article presents the findings of a panel of experts, the Industrial Health Foundation panel, who were charged to identify an OEL that would prevent irritation. To accomplish this task, they critiqued approximately 150 scientific articles. Unlike many other chemicals, a large amount of data is available upon which to base a concentration-response relationship for human irritation. A mathematical model developed by Kane et al. (1979) for predicting safe levels of exposure to irritants based on animal data was also evaluated. The panel concluded that for most persons, eye irritation clearly due to formaldehyde does not occur until at least 1.0 ppm. Information from controlled studies involving volunteers indicated that moderate to severe eye, nose, and throat irritation does not occur for most persons until airborne concentrations exceed 2.0-3.0 ppm. The data indicated that below 1.0 ppm, if irritation occurs in some persons, the effects rapidly subside due to "accommodation." Based on the weight of evidence from published studies, the panel found that persons exposed to 0.3 ppm for 4-6 h in chamber studies generally reported eye irritation at a rate no different than that observed when persons were exposed to clean air. It was noted that at a concentration of 0.5 ppm (8-h TWA) eye irritation was not observed in the majority of workers (about 80%). Consequently, the panel recommended an OEL of 0.3 ppm as an 8-h time-weighted average (TWA) with a ceiling value (CV) of 1.0 ppm (a concentration not to be exceeded) to avoid irritation. The panel believes that the ACGIH TLV of 0.3 ppm as a ceiling value was unnecessarily restrictive and that this value may have been based on the TLV Committee's interpretation of the significance of studies involving self-reported responses at concentrations less than 0.5 ppm. The panel concluded that any occupational or environmental guideline for formaldehyde should be based primarily on controlled studies in humans, since nearly all other studies are compromised by the presence of other contaminants. The panel also concluded that if concentrations of formaldehyde are kept below 0.1 ppm in the indoor environment (where exposures might occur 24 h/d) this should prevent irritation in virtually all persons. The panel could not identify a group of persons who were hypersensitive, nor was there evidence that anyone could be sensitized (develop an allergy) following inhalation exposure to formaldehyde. The panel concluded that there was sufficient evidence to show that persons with asthma respond no differently than healthy individuals following exposure to concentrations up to 3.0 ppm. Although cancer risk was not a topic that received exhaustive evaluation, the panel agreed with other scientific groups who have concluded that the cancer risk of formaldehyde is negligible at airborne concentrations that do not produce chronic irritation.

Animals↗

Oxidation of exogenous formaldehyde in methylotrophic and nonmethylotrophic yeast cells.

Nonmethylotrophic (Candida maltosa and Saccharomyces cerevisiae) and methylotrophic (Hansenula polymorpha) yeast cells acidified their incubation media in the presence of formaldehyde. This was associated with the release of formate. We studied the formaldehyde-dependent production of formic acid and the enzymatic properties of these strains grown on media containing various carbon sources. The acidifying potential was considerably lower in formaldehyde dehydrogenase-deficient cells of mutant strains of H. polymorpha. The rates of acidification by C. maltosa and S. cerevisiae depended on the activity of their nonspecific aldehyde dehydrogenases. We suggest that accumulation of formate by yeast cells incubated in the presence of formaldehyde is caused by the total activity of formaldehyde dehydrogenase and nonspecific aldehyde dehydrogenase in methylotrophic yeasts or aldehyde dehydrogenase only in nonmethylotrophic yeasts. This is probably an additional mechanism for detoxification of formaldehyde.

Aldehyde Dehydrogenase↗

Formaldehyde source interaction studies under whole-house conditions.

This study was designed to determine the effect of source combinations on formaldehyde levels under whole-house conditions. Evaluations were conducted on particleboard (applied as subflooring) and hardwood plywood panelling (applied as a wall covering) both singly and in combination, and on urea-formaldehyde foam insulation and particleboard. Formaldehyde source combination/interaction evaluations revealed several different outcomes, including no augmentation of formaldehyde levels, a slight augmentation (30-50%) and complete addivity. Additivity was observed for regular and low emission grade particleboard and hardwood plywood combinations and for urea-formaldehyde foam insulation and particleboard subflooring. In contrast, controlled chamber studies employing samples of the same wood materials revealed no additive effects. Results of these studies raise questions about the reliability of using laboratory evaluations alone to predict formaldehyde levels under real-world residential conditions.

Journal Article↗

The role of a formaldehyde dehydrogenase-glutathione pathway in protein S-nitrosation in mammalian cells.

Intracellular sulfhydryls, both protein and non-protein, are potential targets of nitric oxide-related species. S-Nitrosation of proteins can occur in vivo and can affect their activity. Metabolic pathways that regulate protein S-nitrosation are therefore likely to be biologically important. We now report that formaldehyde dehydrogenase, an enzyme that decomposes S-nitrosoglutathione, can indirectly regulate the level of cellular protein S-nitrosation. Nitrogen oxide donors induced high levels of protein S-nitrosation in HeLa cells and lower levels in Mutatect fibrosarcoma cells, as determined by Saville-Griess assay and Western-dot-blot analysis. Depletion of glutathione by treatment with buthionine sulfoximine markedly increased protein S-nitrosation in both cell lines. Glutathione depletion also increased cytokine-induced S-nitrosation in brain endothelial cells. Formaldehyde dehydrogenase activity was 2-fold higher in Mutatect than in HeLa cells. We downregulated formaldehyde dehydrogenase activity in Mutatect cells by stably expressing antisense RNA and short-interfering RNA. In these cells, both protein S-nitrosation and S-nitrosoglutathione levels were significantly enhanced after exposure to nitrogen oxide donors as compared to parental cells. Overall, a strong inverse correlation between total S-nitrosothiols and formaldehyde dehydrogenase activity was seen. Inhibition of glutathione reductase, the enzyme that converts oxidized to reduced glutathione, by dehydroepiandrosterone similarly increased protein S-nitrosation and S-nitrosoglutathione levels in both cell lines. Our results provide the first evidence that formaldehyde dehydrogenase-dependent decomposition of S-nitrosoglutathione plays a role in protecting against nitrogen oxide-mediated protein S-nitrosation. We propose that formaldehyde dehydrogenase and glutathione reductase participate in a glutathione-dependent metabolic cycle that decreases protein S-nitrosation following exposure of cells to nitric oxide.

Acetylcysteine↗