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[The cytopathic and cytogenetic sequelae of chronic inhalational exposure to formaldehyde on female germ cells and bone marrow cells in rats].

A study was made of cytopathological and cytogenetic effects of formaldehyde chronic inhalation, in doses 0.5 and 1.5 mg/m3, on the female rat's germ and marrow cells. The harmful effect of formaldehyde on germ cells (according to the patterns of early embryogenesis) is noted under the dose 1.5 mg/m3 only, while the reliable clastogenic and cytogenetic effects on the marrow cells were revealed even in the dose 0.5 mg/m3. It is concluded that the differences between effects of small doses of formaldehyde on different cell systems were evidently caused by the specific cell dynamics of these systems.

Administration, Inhalation↗

Cytotoxicity of glutaraldehyde and formaldehyde in relation to time of exposure and concentration.

The interacting effects of time of exposure and concentration as factors in cytotoxicity were compared for glutaraldehyde and formaldehyde. Cells from a human fibroblast cell line (WI-38) grown to confluence in 24-well trays were exposed to a range of concentrations of each agent, for periods of 4 to 24 hr. Cytotoxicity was measured by its effects on mitochondrial dehydrogenase activity, as assayed biochemically. Cytotoxic effects of formaldehyde occurred over a narrow concentration range from nontoxic to maximally toxic, and the range was little affected by time of exposure. In contrast, glutaraldehyde exerted its effect over a wider concentration range, and longer exposure times were necessary for maximal toxicity. The data suggest that long contact times of glutaraldehyde with dental pulp are necessary for maximum fixation. While 19% formaldehyde appeared to be more toxic than 2.5% glutaraldehyde in terms of serial dilution, little difference in cytotoxicity was observed when the data were calculated in terms of molar concentrations of the two agents.

Cell Line↗

Hygienic aspects of the use of pressed-wood products in residential buildings. Part I. The effect of particleboards ageing on release of formaldehyde.

Urea-formaldehyde-resins bounded particleboards (100 x 40 mm plates) each from a different manufactory plant, were stored at room temperature, with free access of air. In selected time intervals plates were placed in the climatic chamber for five days, and formaldehyde (CH2O) emission were determined. The conditions were as follows: loading factor 1 m2/m3, one air exchange per hour, air temperature of 25 degrees C and relative humidity (RH) 45%. During the 3 months following the production, CH2O emission decreased by more than 50%. During the next months of storing the emission decrease was slight. In the period of 1-3 years since the production, CH2O emission was 0.13-0.06 mg/m2/h, regardless of the amount of formaldehyde released in the first period after the production.

Air Pollution, Indoor↗

[Prevention of formaldehyde-induced occupational dermatoses in health care personnel].

Prevention of Occupational Dermatoses due to Formaldehyde in Employees of the Public Health System Occupational dermatoses lead all occupational diseases in employees of the Public Health and Social System in the district of Schwerin from 1977 to 1985. Disinfectants with formaldehyde which mainly produced allergic dermatoses were the main reasons. By substitution of formaldehyde as disinfectant and the accomplishing of contact-free technologies for cleaning purposes, occupational skin diseases in employees of the Public Health and Social System could obviously be reduced.

Dermatitis, Contact↗

[Cyclic pathway of formaldehyde oxidation in Pseudomonas oleovorans].

Operation of the dissimilatory hexulose phosphate cycle of formaldehyde oxidation in Pseudomonas oleovarans has been directly confirmed. Extracts of this typical facultative methylotroph catalyze the formation of 14CO2 from 14C-formaldehyde. The process depends on the presence of ribose-5-phosphate, NADP or NAD, and is linear in time. Oxidation of formaldehyde via formate to CO2 is of a minor importance in the energy metabolism of the methylotroph.

Formaldehyde↗

Analysis of proteins cross-linked to DNA after treatment of cells with formaldehyde, chromate, and cis-diamminedichloroplatinum(II).

The proteins cross-linked to the DNA of cultured Chinese hamster ovary cells after exposure to cis-diamminedichloroplatinum(II) (cis-Pt), chromate, and formaldehyde were compared by two-dimensional (2D) gel electrophoresis, immunoblotting, and centrifugal assays that measured cross-link stability. Chromate and cis-Pt cross-linked seven of the same nonhistone proteins, such as actin, to DNA. In contrast, formaldehyde selectively formed histone-DNA cross-links. Immunoblotting experiments showed that all three chemicals cross-linked a 97-kDa nuclear protein to the DNA despite their different chemical reactivity with DNA and proteins. The chromate- and cis-Pt-induced cross-links were disrupted by thiourea, 2-mercaptoethanol, and EDTA, indicating that the metal could be chemically displaced from the cross-links. The formaldehyde-induced complexes required degradation with DNase 1 for the resolution of histones on 2D gels and were not chemically labile like the metal-induced cross-links. The agents and methodology used here could be applied to the study of additional nuclear proteins that bind or reside near the DNA.

Animals↗

Liquid chromatographic determination of total formaldehyde in drinking water.

Formaldehyde is readily quantitated at micrograms/L levels in drinking water. The analyte present in 1 L water samples is derivatized with 2,4-dinitrophenylhydrazine in a 2M acid medium and then extracted with chloroform. After the solvent is exchanged for methanol, the product is separated and quantitated using reverse-phase liquid chromatography with UV detection (365 nm). Reporting limits as low as 20 micrograms/L (corrected for laboratory blank) are routinely achieved. Formaldehyde recovery typically exceeds 90% at 20-200 micrograms/L. The method was applied to hot and cold water samples from thirty-four 1- and 2-story houses equipped with poly(acetal) plumbing elbows and tees. The drinking water samples were accompanied by sets of blanks and spikes specified by a quality assurance/quality control plan. Formaldehyde was observed above the reporting limit in 80% of hot and cold water samples from the 1-story dwellings, but in less than 50% of those from the 2-story dwellings. The results may depend on both the construction of the houses (1- vs 2-story) and the time of year the water is sampled (mid-summer).

Chromatography, Liquid↗

Pharmacokinetic and deuterium isotope effect studies on the metabolism of formaldehyde and formate to carbon dioxide in rats in vivo.

The effect of deuterium substitution on the metabolism of formaldehyde and formate to carbon dioxide in vivo was examined. Four groups of male Sprague-Dawley rats were injected ip with carbon-14-labeled formaldehyde, formaldehyde-d2, sodium formate, or sodium formate-d at doses of 0.67 mmol/kg. Similar rates of labeled carbon dioxide exhalation were observed for the four groups of animals, the cumulative excretion of 14CO2 in breath reaching 68-71% of the theoretical value 12 hr after injection in all cases. Plots of amount remaining to be excreted showed that the metabolism was biexponential, with half-lives of approximately 0.4 and 3 hr for the two phases for each of the four compounds. Competitive experiments in which equimolar mixtures of CH2O with CD2O or HCO2- with DCO2- were injected also failed to reveal a substantial isotope effect, although the cumulative conversion of formate to carbon dioxide was significantly higher than that of its deuterated analog at four time points in the middle of the 8-hr mixed-isotope experiment. The data indicate that deuterium substitution has little or no effect on the rates and extents of in vivo oxidation of these 1-carbon species to carbon dioxide, although a small decrease of up to 10% in reactivity under the conditions employed cannot be excluded. The results support the use of carbon dioxide exhalation data in the measurement of deuterium isotope effects on oxidative demethylation reactions such as those that occur in the activation of the carcinogen, N-nitrosodimethylamine.

Animals↗

Effects of formaldehyde on normal xenotransplanted human tracheobronchial epithelium.

Epithelial cells obtained from autopsies of full-term fetuses or infants less than 1 year old were isolated, amplified in primary cultures and inoculated in deepithelialized rat tracheas. These tracheas were then sealed and transplanted subcutaneously into irradiated athymic nude mice. Four weeks after transplantation the tracheal lumen was completely covered by epithelium, most of which was of mucociliary respiratory type. At this stage, tracheal transplants containing tracheobronchial epithelium from 20 different donors were exposed to silastic devices containing 0, 0.5, 1 and 2 mg paraformaldehyde. The tracheal transplants were examined histologically at 2, 4, 8, and 16 weeks after transplantation. Before sacrifice, all animals were injected with a single pulse of tritiated thymidine. Important epithelial alterations could be seen in the formaldehyde treated transplants with a maximum effect visible at 2 weeks after exposure. The highest dose of 2 mg produced, in most cases, numerous areas of epithelial erosion and inflammation whereas this effect was not as evident with the lower doses. All doses produced areas of hyperplastic epithelium alternating with areas of pleomorphic-atrophic epithelium. Although the differences in predominance of different types of epithelium was not clearly dose-dependent, the labeling index (LI) showed dose dependence between 2 and 4 weeks after initiation of exposure. The maximum mean LI was three to four times higher than normal, although in some focal hyperplastic-metaplastic lesions the LI was increased up to 20 times. These studies show that formaldehyde, although toxic at higher doses, is able to elicit at lower doses a proliferative response of the human respiratory epithelium that is not preceded by a massive toxic effect. This response is similar, although less intense than that of the rat respiratory epithelium in which formaldehyde proved to be a carcinogen.

Animals↗

Conditions for proper formaldehyde inactivation of foot and mouse disease alhydrogel vaccines.

The inactivation of FMDV by formaldehyde (FA) was studied under different conditions, both as free virus and (as in routine vaccine production) after adsorption of the virus to aluminium hydroxide gel (alhydrogel). In the latter case infectivity was monitored after elution of the virus from the gel by isopycnic ultracentrifugation of the virus-alhydrogel mixture in CsCl. By this method good virus recoveries were obtained. Adsorption of the virus to alhydrogel (without formaldehyde) did not reduce infectivity significantly. Both adsorbed and non-absorbed virus lost infectivity at a rate of about one log10 per day (at pH 8.5, 25 degrees C - no formaldehyde). Kinetics of FA inactivation of adsorbed and non-adsorbed virus were also identical, with a fast reduction in the initial phase. After this initial phase inactivation became linear and rather slow. No 'tailing-off' was observed. Some additives (f.i. LAH and especially Tris) reduced the inactivation rate. These findings might explain some data of others who observed 'tailing-off'.

Adsorption↗

[Inactivation of formaldehyde by semicarbazide in disinfectant tests with viruses].

In suspension tests with viruses formaldehyde is--even in weak concentrations--toxic for tissue cultures. Through addition of semicarbazide in a ratio of one part of 10% semicarbazide to one part of 0.7% formaldehyde, which is equivalent to a molar ratio of 3.8:1, the toxicity will be neutralized if semicarbazide is added to the tissue cultures before their being inoculated with the virus-disinfectant-mixture. In qualitative experiments the toxicity is completely neutralized, in quantitative ones it is reduced by a factor of 10 up to 100. Thus the evaluation of the virucidal capacity of disinfectants containing formaldehyde is conspicuously improved.

Adenoviridae↗

Interactive effects of duration of storage and addition of formaldehyde on levels of aflatoxin M1 in milk.

Spray-dried skim milk, naturally contaminated with aflatoxin M1, was added to either raw or pasteurized whole milk to a final concentration of 1.1 microgram aflatoxin M1/L milk. Formalin (37% w/w) was added to the milk solutions to final concentrations of 0, 0.025, 0.05, and 0.1% formaldehyde. Samples were stored in the dark at 21 degrees C in plastic and glass containers and were analyzed for aflatoxin M1 at 0, 1, 2, 3, and 4 weeks. This experiment was repeated using only raw milk and glass containers. Aflatoxin M1 analyses were done at 0, 1, and 2 weeks. Aflatoxin M1 losses increased over time and with increased formaldehyde concentration. With both experiments, aflatoxin M1, levels after 2 weeks were less than 0.05 micrograms/L in samples containing 0.1% formaldehyde.

Aflatoxin M1↗

[Chronic formaldehyde exposure--a misunderstood disease?].

A family with chronic exposure to formaldehyde in a renovated apartment is reported. The source of exposure proved to be chipboard. The family members' symptoms were eye and upper airway irritation, malaise, headache, nausea, sleeping disturbances, irritability and lack of appetite. At first the syndrome was thought to be psychosomatic and the correct diagnosis was overlooked. Ten years after beginning of the chronic exposure a formaldehyde level of 0.35 ppm was still recorded in the apartment. Sources, symptoms and diagnosis of chronic formaldehyde immission are discussed.

Adult↗

Gas chromatographic determination of formaldehyde in maple syrup as 2,4-dinitrophenylhydrazone derivative.

A procedure is presented for the quantitative extraction and determination of formaldehyde in maple sap and syrup. The method is based on the reaction between formaldehyde and 2,4-dinitrophenylhydrazine and determination of the derivative by gas chromatography. The procedure was used to evaluate formaldehyde in saps and syrups of paraformaldehyde implanted trees. Average recoveries were 101.5 +/- 5.7%. The detection limit was 0.078 mg/kg.

Chromatography, Gas↗

[Lethal effect of formaldehyde on Escherichia coli strains carrying or lacking the plasmid pKM101].

The presence of plasmid pKM101 in Escherichia coli cells results in a slight increase in their sensitivity of lethal effect of formaldehyde. Plasmid ability to sensitize bacterial cells to formaldehyde inactivation is controlled by some chromosomal (uvrE, uvrA, recA) and plasmid-borne (mucAB) genes and depends on SOS-DNA repair activity. Plasmid pKM101 is capable of decreasing the level of repair reliability of DNA damaged by formaldehyde thus causing increased bacterial sensitivity to this agent.

Drug Resistance, Microbial↗

Removing formaldehyde from embalmed cadavers by percolating the body cavities with dilute ethanol.

Formaldehyde was removed from embalmed animal cadavers by pumping ethanol (20%) through the pleural and peritoneal cavities of 4 goats, 4 cows and 4 horses. The goats were percolated intermittently for 7 days and the large animals continuously for 72 h. Just after opening the body cavities, samples of air close to the organs were collected and analyzed for formaldehyde using a spectrofluorimetric method. The concentration of formaldehyde in the air samples was in goats 0.45 +/- 0.44 microgram/l (mean +/- SD), cows 0.42 +/- 0.29 microgram/l and horses 0.43 +/- 0.25 microgram/l.

Air↗

Influence of intraperitoneally administered formaldehyde on bile production and tissue glutathione levels in rats.

The influence of formaldehyde on bile secretion and tissue glutathione concentrations was investigated in male Sprague Dawley rats following a sublethal intraperitoneal administration (72 mg/kg). Within 2-3 h of administration formaldehyde caused a 2-fold increase in secretion of bile and significant decrease in the levels of glutathione in liver (39% of control) followed by kidney (33%), lung (31%) and brain (22%). The results indicate a possible protective role of glutathione in the toxicity of formaldehyde.

Animals↗