Search PubMed⌕ Search

SEARCH · Search PubMed

Results for “Propanols”

Search indexed PubMed citations on genomics, clinical trials, systematic reviews and public health. Explore titles, authors and supplied subject terms, then open the PubMed record.

Quote a phrase for an exact phrase match. Source license links do not imply unrestricted reuse.

At least 19 recordsLinked to original sources
PubMed2006

The analysis of 1-propanol and 2-propanol in humid air samples using selected ion flow tube mass spectrometry.

Following the observation that propanol is present in the breath samples of cystic fibrosis (CF) patients infected by Pseudomonas aeruginosa (PA), a study of the reactions of H(3)O(+), NO(+) and O(2) (+.) with 1-propanol and 2-propanol has been conducted using selected ion flow tube mass spectrometry (SIFT-MS). In this study the number and the distribution of the product ions from NO(+) reactions with the two propanol isomers under humid air conditions were able to differentiate between the two isomers. The reaction mechanisms and the structures of the product ions for these reactions, especially those with H(3)O(+) and NO(+), have been proposed. As an example, 2-propanol was shown to be present in a breath sample from one CF patient infected with PA, and also in a PA isolate from another CF patient grown on Pseudomonas-selective media. The results of this study allow an analytical procedure to be advanced for the analysis of the two propanol isomers, which can also be utilised in other applications.

1-Propanol↗
PubMed2005

Evaluation of exposure to 1-alkoxy-2-propanols and 1-(2-methoxy-1-methylethoxy)-2-propanol by the analysis of the parent compounds in urine.

Floor lacquerers' inhalation and total exposure to 1-alkoxy-2-propanols and 1-(2-methoxy-1-methylethoxy)-2-propanol (DPGME) were measured. The total exposure was biomonitored by urinalysis of free unchanged 1-alkoxy-2-propanols and DPGME. The floor lacquerers' 8-h inhalation exposures to 1-methoxy-2-propanol (PGME), 1-butoxy-2-propanol (PGBE) and DPGME were 1.9+/-1.3 (mean+/-S.D., n=15), 1.0+/-1.4ppm (n=11) and 0.2+/-0.3ppm (n=11), respectively. The gravity-corrected urinary excretions of PGME, PGBE and DPGME were 5.3+/-5.4mumol/l, 0.9+/-0.9mumol/l and 1.5+/-2.8mumol/l, respectively. A linear relationship was found between the gravity-corrected urinary excretion of PGME (R(2)=0.82), PGBE (R(2)=0.93) and DPGME (R(2)=0.93) and their preceding 8-h inhalation exposure. The correlations between the uncorrected urinary excretions and inhalation exposures to PGME, PGBE and DPGME was also calculated and found good (R(2)=0.82-0.95). The effect of work strain on the total exposure seemed to be more relevant in the exposure to hydrophilic PGME than in the exposure to more lipophilic PGBE.

Air Pollutants, Occupational↗
PubMed1999

The reaction of thiolates with 2,3-dibromo-1-propanol revisited: application to the synthesis of bis(fattyalkylthio)propanols.

This work compares two reaction schemes for preparing 2,3-bis(fattyalkylthio)-1-propanols for further synthetic adaptation as hydrophobic analogs of lung surfactant phosphatidylcholines. An attempt to prepare 2,3-bis(fattyalkylthio)-1-propanols based on the previously published methods of Bell and co-workers (B.R. Ganong, C.R. Loomis, Y.A. Hannun, R.M. Bell, 1986. Proc. Natl. Acad. Sci. USA 83, 1184-1188; B.R. Ganong, R.M. Bell, 1987. Methods Enzymol. 141, 313-320; J.P. Walsh, L. Fahrner, R.M. Bell, 1990. J. Biol. Chem. 265, 4374-4381) was found to give the rearranged 1,3-bis(fattyalkylthio)-2-propanols as major products. As a reliable alternative, the reaction of ethyl 2,3-dibromopropionate with 2 equivalents of long chain sodium n-alkanethioates gave the corresponding ethyl 2,3-bis(n-alkylthio)propionates, which were then reduced with LiAlH4 to yield the desired 2,3-bis(fattyalkylthio)-1-propanols. Both 13C and 1H NMR spectroscopy were used to differentiate the two possible 1,3- and 2,3-dithio substituted alcohol products and to rigorously assign their structures.

Magnetic Resonance Spectroscopy↗
PubMed1990

Anticholinergic agents. 2. Absolute configurations of 2-methyl-1,1-diphenyl-3-(1-piperidyl)-1-propanol and 2-methyl-1,1-diphenyl-3-(1-pyrrolidyl)-1-propanol. Crystal structures of the corresponding mandelates.

Racemic 2-methyl-1,1-diphenyl-3-(1-piperidyl)-1-propanol (4) and 2-methyl-1,1-diphenyl-3-(1-pyrrolidyl)-1-propanol (5) have been synthesized and optically resolved employing (R)- and (S)-mandelic acid, respectively, as resolving agents. The absolute configurations of the enantiomers of 4 and 5 have been established as (-)-(R) and (+)-(S) by crystal structure analyses of (-)-(R)-2-methyl-1,1-diphenyl-3-(1-piperidinio)-1-propanol (+)-(S)-mandelate and (+)-(S)-2-methyl-1,1-diphenyl-3-(1-pyrrolidinio)-1-propanol (-)-(R)-mandelate. The corresponding methiodides have been prepared.

Crystallography↗
PubMed2006

Gas phase infrared multiple-photon dissociation spectra of methanol, ethanol and propanol proton-bound dimers, protonated propanol and the propanol/water proton-bound dimer.

The infrared multiphoton dissociation (IRMPD) spectra of three homogenous proton-bound dimers are presented and the major features are assigned based on comparisons with the neutral alcohol and with density functional theory calculations. As well, the IRMPD spectra of protonated propanol and the propanol/water proton-bound dimer (or singly hydrated protonated propanol) are presented and analysed. Two primary IRMPD photoproducts were observed for each of the alcohol proton bound dimers and were found to vary with the frequency of the radiation impinging upon the ions. For example, when the proton-bound dimer absorbs weakly a larger amount of S(N)2 product, protonated ether and water, are observed. When the proton-bound dimer absorbs more strongly, an increase in the simple dissociation product, protonated alcohol and neutral alcohol, is observed. With the aid of RRKM calculations this frequency dependence of the branching ratio is explained by assuming that photon absorption is faster than dissociation for these species and that only a few photons extra are necessary to make the higher-energy dissociation channel (simple cleavage) competitive with the lower energy (S(N)2) reaction channel.

1-Propanol↗
PubMedDate not supplied

Effects of novel safrole oxide derivatives, 1-propyl-3-(3,4-methylenedioxyphenyl)-2-propanol and 1-isopropoxy-3-(3,4-methylenedioxyphenyl)-2-propanol, on apoptosis induced by deprivation of survival factors in vascular endothelial cells.

Two safrole oxide derivatives, 1-propoxy-3-(3,4-methylenedioxyphenyl)-2-propanol (FOD) and 1-isopropoxy-3-(3,4-methylenedioxyphenyl)-2-propanol (GOD), were newly synthesized as promoters of apoptosis in vascular endothelial cells. The purpose of this study was to investigate the effects of these two safrole oxide derivatives on cell growth and apoptosis induced by deprivation of survival factors (serum and fibroblast growth factors, aFGF and bFGF) in vascular endothelial cells (VECs). MTT (3-[4,5-dimethylthiazol-2-yl]-2,5-diphenyltetrazolium) method, agarose gel electrophoresis, laser scanning confocal microscopy, flow cytometry (FCM), and immunofluorescence assay were used. The cells deprived of FGF and serum were exposed to FOD or GOD 30 to 90 mg x L(-1) for 24 h, cell growth was suppressed (p < .05), whereas detachment and DNA fragmentation of these cells were promoted (p < .01). When the cells were treated with FOD 90 mg x L(-) for 24 h, apoptosis rate was 14.99% (p < .01). There were more cells in G2-M phase and less cells in S phase. At 90 mg x L(-1) concentration, GOD blocked 77.03%of the cells at G0-G1 phase., P53 level in VEC exposed to FOD or GOD was increased (p < .01). The data suggested that FOD and GOD might promote apoptosis of VEC by affect the cell cycle distribution, whereas P53 was involved in this pathway.

Apoptosis↗
PubMed2003

Effects of novel safrole oxide derivatives, 1-methoxy-3-(3,4-methylenedioxyphenyl)-2-propanol and 1-ethoxy-3-(3,4-methylenedioxyphenyl)-2-propanol, on apoptosis induced by deprivation of survival factors in vascular endothelial cells.

Two safrole oxide derivatives, 1-methoxy-3-(3,4-methylenedioxyphenyl)-2-propanol (MOD) and 1-ethoxy-3-(3,4-methylenedioxyphenyl)-2-propanol (EOD), were newly synthesized as promoters of apoptosis in vascular endothelial cells (VECs). The purpose of this study was to investigate the effects of these two safrole oxide derivatives on cell growth and apoptosis induced by deprivation of survival factors (serum and fibroblast growth factors, aFGF and bFGF) in VECs. Morphological changes were observed with light microscopy. Cell growth was determined by using MTT (3-[4, 5-dimethyl thiazol-2-yl]-2, 5-diphenytetrazolium) method. DNA fragmentation was analyzed by agarose gel electrophoresis and fluorescence microscopy. Apoptosis rate and cell cycle distribution were analyzed by flow cytometry (FCM). The cells deprived of FGF and serum were exposed to MOD 10-40 mg l(-1) for 24 h. Cell growth was suppressed (P<.01), while detachment and DNA fragmentation of these cells were promoted (P<.01). When the cells were treated with MOD30 mg l(-1) for 24 h, apoptosis rate was 21.43% (P<.01). The fact that 66.50% of the cells were trapped in S phase of cell cycle indicated that the cell cycle was blocked at S phase. Treated with EOD 10-40 mg l(-1) for 24 h, the cells were observed; the results showed that VEC growth was inhibited and the apoptosis was triggered (P<.01). At 30 mg l(-1) concentration, EOD blocked 55.22% of the cells at S phase. The data suggested that MOD and EOD might promote apoptosis of VEC by blocking the cell cycle at S phase.

Apoptosis↗
PubMed1977

beta-Adrenergic blocking agents. 17. 1-Phenoxy-3-phenoxyalkylamino-2-propanols and 1-alkoxyalkylamino-3-phenoxy-2-propanols.

The synthesis is described of a series of derivatives of 1-phenoxy-3-phenoxyalkylamino-2-propanols and 1-alkoxyalkylamino-3-phenoxy-2-propranols. The compounds were investigated for their beta-adrenoceptor blocking properties and many showed a surprising degree of cardioselectivity when tested in vivo in anesthetized cats for their effects on an isoproterenol-induced tachycardia and depressor response. The structure-activity relationship shown by this series of compounds is related to that of known cardioselective analogues and a possible reason for their cardioselectivity is discussed.

Adrenergic beta-Antagonists↗
PubMed1998

NTP Toxicology and Carcinogenesis Studies of 1-Chloro-2-propanol (Technical Grade) (CAS NO. 127-00-4) in F344/N Rats and B6C3F1 Mice (Drinking Water Studies.

1-Chloro-2-propanol and its positional isomer, 2-chloro-1-propanol, are used as chemical intermediates for the manufacture of propylene oxide, a starting material for production of polyurethane polyols and propylene glycol. The National Cancer Institute nominated 1-chloro-2-propanol for study because of potential for human exposure due to its residues in various foods that are fumigated with ethylene oxide or propylene oxide. Male and female F344/N rats and B6C3F1 mice were exposed to technical grade 1-chloro-2-propanol (75% to 76%% 1-chloro-2-propanol; 24% to 25%% 2-chloro-1-propanol) in drinking water for 14 days, 14 weeks, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, Drosophila melanogaster, and mouse peripheral blood erythrocytes. Continuous breeding studies were conducted in Sprague-Dawley rats. 14-DAY STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were administered 1-chloro-2-propanol in drinking water at concentrations of 0, 100, 330, 1,000, 3,300, or 10,000 ppm for 14 days. Two 10,000 ppm females died before the end of the study. The final mean body weights and body weight gains of 3,300 and 10,000 ppm rats were significantly less than those of the controls; rats in the 10,000 ppm groups lost weight. Water consumption by the 3,300 and 10,000 ppm groups was significantly less than that by the controls throughout the study. The thymus weights of 10,000 ppm rats were significantly less than those of the controls. Exposure to 1-chloro-2-propanol caused cytoplasmic alteration and degeneration of the acinar cells and fatty change in the pancreas, atrophy of the bone marrow, and atrophy and hematopoiesis of the spleen in males and females. 14-DAY STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were administered 1-chloro-2-propanol in drinking water at concentrations of 0, 100, 330, 1,000, 3,300, or 10,000 ppm for 14 days. One male mouse in the 10,000 ppm group died before the end of the study. Mean body weight gains of 10,000 ppm mice were significantly less than those of the controls. Water consumption by 3,300 and 10,000 ppm males and females was significantly less than that by the controls throughout the study. Liver weights of 1,000, 3,300, or 10,000 ppm males and females were significantly greater and thymus weights of 10,000 ppm mice were significantly less than those of the controls. Exposure to 1-chloro-2-propanol caused hepatocellular vacuolization, cytoplasmic alteration and degeneration of the pancreas acinar cells, and atrophy of the spleen in males and females. 14-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were administered 1-chloro-2-propanol at concentrations of 0, 33, 100, 330, 1,000, or 3,300 ppm (equivalent to average daily doses of approximately 5, 10, 35, 100, or 220 mg/kg) for 14 weeks. All rats survived to the end of the study. Mean body weight gains of 3,300 ppm rats were significantly less than those of the controls. Water consumption by the 3,300 ppm male and female rats was significantly less than that by the controls. A minimal to mild anemia was observed in exposed female rats. The cauda epididymis and epididymis weights of 3,300 ppm males were significantly less than those of the controls. The percentage of abnormal sperm in 3,300 ppm males and the concentration of epididymal sperm in 330 ppm males were significantly increased compared to the controls. Kidney and liver weights of males and females exposed to 100 ppm or more were generally greater than those of the controls. The incidences of acinar cell degeneration and fatty change of the pancreas in 1,000 and 3,300 ppm rats, hepatocytic metaplasia of the pancreatic islets in 3,300 ppm females, cytoplasmic vacuolization of the liver in 100, 1,000 and 3,300 ppm males, and renal tubule epithelium regeneration in 3,300 ppm females were increased compared to the controls. 14-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were administered 1-chloro-2-propanol in drinking water at concentrations of 0, 33, 100, 33entrations of 0, 33, 100, 330, 1,000, or 3,300 ppm (equivalent to average daily doses of approximately 5, 15, 50, 170, or 340 mg/kg to males and 7, 20, 70, 260, or 420 mg/kg to females) for 14 weeks. One 330 ppm male died before the end of the study. Mean body weight gains of exposed groups were similar to those of the controls. A minimal anemia was observed in 3,300 ppm males. The right epididymis weight of 3,300 ppm males was significantly greater than that of the controls. Kidney weights of 3,300 ppm mice, liver weights of 1,000 ppm males and of all exposed groups of females, and thymus weights of 1,000 and 3,300 ppm females were greater than those of the controls. The incidences of pancreatic acinar cell degeneration and fatty change in 3,300 ppm males and females and cytoplasmic vacuolization of the liver in all groups of exposed females were significantly increased compared to the controls. The severities of renal tubule cytoplasmic vacuolization were greater in 1,000 and 3,300 ppm males than in the controls. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female F344/N rats were administered drinking water containing 0, 150, 325, or 650 ppm 1-chloro-2-propanol (equivalent to average daily doses of approximately 15, 30, or 65 mg/kg during the first several months of the study and 8, 17, or 34 mg/kg for the remainder of the 2-year study) for up to 105 weeks. Survival of all exposed groups was similar to that of the controls. Mean body weights of exposed rats were generally similar to those of the controls throughout most of the study. Water consumption by all exposed groups was similar to that by the controls. No treatment-related neoplasms or nonneoplastic lesions were observed in this study. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female B6C3F1 mice were administered drinking water containing 0, 250, 500, or 1,000 ppm 1-chloro-2-propanol (equivalent to average daily doses of approximately 45, 75, or 150 mg/kg to males and 60, 105, or 210 mg/kg to females during the first several months of the study and 25, 50, or 100 mg/kg for the remainder of the 2-year study) for up to 105 weeks. Survival of all exposed groups was similar to that of the controls. The mean body weights of all exposed mice were generally similar to those of the controls throughout the study. Water consumption by all exposed groups was similar to that by the controls. No treatment- related neoplasms or nonneoplastic lesions were observed in this study. GENETIC TOXICOLOGY: 1-Chloro-2-propanol is a demonstrated mutagen in vitro. It was weakly mutagenic in S. typhimurium strain TA100 in the presence of hamster or rat liver S9 activation enzymes and was positive, with and without S9, in TA1535. No mutagenic activity was detected in strains TA97, TA98, and TA1537, with or without S9. In cytogenetic tests with Chinese hamster ovary cells, 1-chloro-2-propanol induced high levels of sister chromatid exchanges and chromosomal aberrations in the presence and the absence of S9. The marked ability of 1-chloro-2-propanol to induce chromosomal effects in vitro was not seen in vivo. Positive results were obtained in a test in D. melanogaster for induction of sex-linked recessive lethal mutations in germ cells of males administered 1-chloro-2-propanol via injection; however, negative results were obtained when males were administered 1-chloro-2-propanol in feed. A subsequent germ cell reciprocal translocation test in D. melanogaster yielded negative results. Further, no induction of micronucleated erythrocytes was observed in peripheral blood of male and female mice administered 1-chloro-2-propanol via drinking water for 14 weeks. CONCLUSIONS: Under the conditions of these 2-year drinking water studies, there was no evidence of carcinogenic activity of technical grade 1-chloro-2-propanol in male or female F344/N rats exposed to 150, 325, or 650 ppm. There was no evidence of carcinogenic activity of technical grade 1-chloro-2-propanol in male or female B6C3F1 mice exposed to 250, 500, or 1,000 ppm. Synonyms: 1-Chloro-2-hydroxypropane, 1-chloroisopropyl alcohol, propylene-&alpha;-chlorohydrin, sec-propylene chlorohydrin

Journal Article↗
PubMed1993

NTP Toxicology and Carcinogenesis Studies of 2,3-Dibromo-1-Propanol (CAS No. 96-13-9) in F344/N Rats and B6C3F1 Mice (Dermal Studies).

2,3-Dibromo-l-propanol, a colorless liquid, has been used as a flame retardant, as an intermediate in the preparation of the flame retardant tris(2,3-dibromopropyl) phosphate, and as an intermediate in the manufacture of pesticides and pharmaceutical preparations. Toxicology and carcinogenicity studies were conducted by applying 2,3-dibromo-1-propanol (approximately 98% pure) in ethanol to the subscapular area of the skin of male and female F344/N rats and B6C3F1 mice 5 days per week for 16 days, 13 weeks, 48 to 51 weeks (male rats), 52 to 55 weeks (female rats), 36 to 39 weeks (male mice), or 39 to 42 weeks (female mice). Genetic toxicology studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, Drosophila melanogaster, mouse Iymphoma cells, and mouse bone marrow cells. 16-DAY STUDY IN RATS Groups of five male and five female rats received dermal applications of 0, 44, 88, 177, 375, or or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 16 days. One male and one female receiving 750 mg/kg died before the end of the study. The mean body weight gains and final mean body weights of dosed rats were similar to those of the controls. There were no clinical findings or gross lesions associated with chemical application. 16-DAY STUDY IN MICE Groups of five male and five female mice received dermal applications of 0, 44, 88, 177, 375, or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 16 days. Four males and one female receiving 750 mg/kg died before the end of the study. The mean body weight gains and final mean body weights of dosed mice were similar to those of the controls. There were no clinical findings or gross lesions associated with chemical application. 13-WEEK STUDY IN RATS Groups of 10 male and 10 female rats received dermal applications of 0, 44, 88, 177, 375, or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 13 weeks. All rats survived until the end of the for 16 days. One male and one female receiving study. For rats in the 750 mg/kg groups, the mean 750 mg/kg died before the end of the study. The body weight gain was 11% lower than that of the controls for males and 13% lower for females. The mean liver weights and liver-weight-to-body-weight ratios of males receiving 375 or 750 mg/kg and of females receiving 750 mg/kg were increased. Chemical-related lesions occurred in the kidney of male rats and in the liver of female rats. The average severity of nephropathy was slightly increased in males receiving dermal applications of 750 mg/kg, while individual cell necrosis was observed in the liver of all female rats in the 750 mg/kg group. 13-WEEK STUDY IN MICE Groups of 10 male and 10 female mice received dermal applications of 0, 44, 88, 177, 375, or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 13 weeks. Eight male mice receiving 750 mg/kg died during the study, while all female mice survived. The final mean body weights of dosed and control mice were similar. The mean liver weights and liver weight-to-body-weight ratios of males receiving 375 or 750 mg/kg and of females receiving 750 mg/kg were increased. Chemical-related lesions occurred in the liver and lung of mice. Centrilobular hepatocellular necrosis occurred in all males in the 750 mg/kg group that died during the study, while individual cell necrosis was observed in the liver of females receiving 177, 375, or 750 mg/kg. Pleomorphism of the epithelium in pulmonary bronchioles occurred with a dose related increased incidence in males and females. Necrosis of the bronchiolar epithelium was observed in males receiving 750 mg/kg. LONG-TERM STUDY IN RATS Originally planned to last for 2 years, the chronic study in rats was terminated early because of reduced survival in the high-dose groups related to chemical induced neoplasms and because of the detection of antibodies to Iymphocytic choriomeningitis virus in sentinel mice. Groups of 50 male and 50 female rats received dermal applications of 0,188, or 375 mg/kg 2,3-dibromo-1-propanol 5 days per week for 48 to 51 weeks (males) or 52 to 55 weeks (females). Su5 weeks (females). Survival, Body Weights, and Clinical Findings The survival of 375 mg/kg male and female rats was significantly lower than that of the controls (males: 50/50, 41/50,16/50; females: 48/50, 38/50, 24/50). In the 375 mg/kg groups, the final mean body weight was 23&percnt; lower than that of the controls for males and 14&percnt; lower for females. There were no chemical related clinical findings. Pathology Findings Application of 2,3-dibromo-1-propanol to the skin produced significant dose-related increases in the incidences of neoplasms at numerous sites in male and female rats. Almost all dosed rats had malignant neoplasms; only one control male and one control female had malignant neoplasms. In male rats, the incidences of benign or malignant neoplasms of the skin, nose, Zymbal's gland, oral mucosa, esophagus, and small and large intestines were significantly increased in the low- and high-dose groups, while the incidences of neoplasms of the forestomach and liver were significantly increased only in the high-dose group. Neoplasms of the kidney, vascular neoplasms of the spleen, and mesotheliomas in males occurred with a significant positive trend. In female rats, the incidences of benign or malignant neoplasms of the nose, Zymbal's gland, oral mucosa, esophagus, large intestine, and liver were significantly increased in the low- and high-dose groups, while the incidences of neoplasms of the skin, forestomach, small intestine, mammary gland, and clitoral gland were significantly increased in the high-dose group only. Neoplasms of the kidney in females occurred with a significant positive trend. LONG-TERM STUDY IN MICE Originally planned to last for 2 years, the chronic study in mice was terminated early because of the detection of antibodies to lymphocytic choriomeningitis virus in sentinel mice. Groups of 50 male and 50 female mice received dermal applications of 0, 88, or 177 mg/kg 2,3-dibromo-1-propanol 5 days per week for 36 to 39 weeks (males) or 39 to 42 weeks (females). Survival, Body Weights, and Clinical Findings All mice (except two low-dose females) survived until study termination. Mean body weights of control and dosed mice were similar throughout the study, and there were no clinical findings attributed to 2,3-dibromo-l-propanol. Pathology Findings Application of 2,3-dibromo-1-propanol to the skin produced significant dose-related increases in the incidences of neoplasms at several sites in male and female mice. Benign or malignant neoplasms were observed in 40&percnt; of the low-dose males, 66&percnt; of the high-dose males, 52&percnt; of the low-dose females, and 56&percnt; of the high-dose females. In control groups, neoplasms occurred in 6&percnt; of the males and 10&percnt; of the females. In male and female mice, the incidences of benign or malignant neoplasms of the forestomach were significantly increased in the low- and high-dose groups, while the incidences of neoplasms of the skin were significantly increased only in the high-dose groups. The incidences of liver and lung neoplasms were increased in high-dose males. GENETIC TOXICOLOGY 2,3-Dibromo-l-propanol was mutagenic in a variety of short-term tests, independent of exogenous metabolic activation (S9). It induced gene mutations in three strains of Salmonella typhimurium (TA98, TA100, and TA1535) and was positive in the mouse Iymphoma assay for induction of trifluorothymidine resistance in L5178Y cells. 2,3-Dibromo-l-propanol induced sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells. In germ cells of male Drosophila melanogaster, 2,3-dibromo-1-propanol induced sex-linked recessive lethal mutations and reciprocal translocations. Results of an in vivo bone marrow micronucleus assay in male mice treated with 2,3-dibromo-1-propanol were negative. CONCLUSIONS Under the conditions of these long-term dermal studies, there was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in male F344/N rats based on increased incidences of neoplasms of the skin, nose, oral mucosa, esophagus, forestomach, small and large intestine, Zymbal's gland, liver, kidney, tunica vaginalis, and spleen. There was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in female F344/N rats based on increased incidences of neoplasms of the skin, nose, oral mucosa, esophagus, forestomach, small and large intestine, Zymbal's gland, liver, kidney, clitoral gland, and mammary gland. There was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in male B6C3F1 mice based on increased incidences of neoplasms of the skin, forestomach, liver, and lung. There was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in female B6C3F1 mice based on increased incidences of neoplasms of the skin and the forestomach. The increased incidences of alveolar/bronchiolar adenomas in female mice may have been related to chemical administration. In rats, 2,3-dibromo-1-propanol caused increased incidences of hyperkeratosis in the skin, forestomach, and esophagus, epithelial dysplasia in the nose, pleomorphism and basophilic and clear cell changes in the liver, and nuclear enlargement in the kidney. There were also chemical-related increases in the incidences of forestomach ulcers and acanthosis, angiectasis in the liver, and renal hyperplasia in male rats and epithelial dysplasia of the forestomach and bile duct hyperplasia in the liver in female rats. Chemical-related increases occurred in the incidences of hyperplasia in the skin, epithelial dysplasia of the forestomach, and bronchiolar epithelial pleomorphism and hyperplasia in male and female mice and in the incidence of eosinophilic cytoplasmic change in the liver in males. Synonyms: 2,3-dibromopropanol; 2,3-dibromopropyl alcohol.

Journal Article↗
PubMed2004

Anaerobic 2-propanol degradation in anoxic paddy soil and the possible role of methanogens in its degradation.

The anaerobic degradation of 2-propanol in anoxic paddy soil was studied with soil cultures and a 2-propanol-utilizing methanogen. Acetone was the first and the major intermediate involved in the methanogenic degradation of 2-propanol. Analyses with a methanogenesis inhibitor, bacteria antibiotics, and the addition of H2 to the gas phase revealed that 2-propanol oxidation to acetone directly occurred using 2-propanol-utilizing methanogens, but not with H2-producing syntrophic bacteria, for which the removal of acetone is required for complete 2-propanol oxidation. The 2-propanol-utilizing strain IIE1, which is phylogenetically closely related to Methanoculleus palmolei, was isolated from paddy soil, and the potential role of the strain in 2-propanol degradation was investigated. 2-Propanol is one of the representative fermentation intermediates in anaerobic environments. This is the first report on the anaerobic 2-propanol degradation process.

2-Propanol↗
PubMed2003

Sex differences in the toxicokinetics of inhaled solvent vapors in humans 2. 2-propanol.

The aim of this study was to evaluate possible sex differences in the inhalation toxicokinetics of 2-propanol vapor. Nine women and eight men were exposed on different occasions for 2 h during light physical exercise (50 W) to 2-propanol (350 mg/m3) and to clean air (control exposure). The level corresponds to the Swedish occupational exposure limit. 2-Propanol and its metabolite acetone were monitored up to 24 h after exposure in exhaled air, blood, saliva, and urine by headspace gas chromatography. Body fat and lean body mass were estimated from sex-specific equations using bioelectrical impedance, body weight, height, and age. Genotypes were determined by PCR-based assays for alcohol dehydrogenase and cytochrome P450 2E1 (CYP2E1). The CYP2E1 phenotype was assessed by the 2-h plasma 6-hydroxychlorzoxazone/chlorzoxazone metabolic ratio in vivo. The toxicokinetic profile in blood was analyzed using a one-compartment population model. The following sex differences were significant at the p = 0.05 level (Student's t test). The respiratory uptake was lower and the volume of distribution smaller in females. The women had a slightly shorter half-time of 2-propanol in blood and a higher apparent total clearance when corrected for body composition. However, women reached approximately four times higher 2-propanol levels in exhaled air at 10-min postexposure and onward. Acetone in blood was markedly higher in females than in males in the control experiment and slightly higher following exposure to 2-propanol. A marked sex difference was that of a 10-fold higher in vivo blood:breath ratio in men, suggesting sex differences in the lung metabolism of 2-propanol. The most marked sex difference was that of salivary acetone, for which an approximately 100-fold increase was seen in women, but no increase in men, after exposure to 2-propanol compared to clean air. The toxicokinetic analysis revealed no significant differences in toxicokinetics between subjects of different metabolic genotypes or phenotypes. In conclusion, the study indicates several sex differences in the inhalation toxicokinetics of 2-propanol. Most of these differences are consistent with anatomical differences between women and men. However, body build can not explain the sex differences in 2-propanol levels in expired air and acetone in saliva.

2-Propanol↗