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At least 19 recordsLinked to original sources
PubMed1975

The EPA National Fuels Surveillance Network. I. Trace constituents in gasoline and commercial gasoline fuel additives.

A National Fuels Surveillance Network has been established to collect gasoline and other fuels through the 10 regional offices of the Environmental Protection Agency. Physical, chemical, and trace element analytical determinations are made on the collected fuel samples to detect components which may present an air pollution hazard or poison exhaust catalytic control devices. A summary of trace elemental constituents in over 50 gasoline samples and 18 commercially marketed consumer purchased gasoline additives is presented. Quantities of Mn, Ni, Cr, Zn, Cu, Fe, Sb, B, Mg, Pb, and S were found in most regular and premium gasoline. Environmental implications of trace constituents in gasoline are discussed.

Air Pollutants↗
PubMed1992

A comparison of European High Test gasoline and PS-6 unleaded gasoline in their abilities to induce alpha 2u-globulin nephropathy and renal cell proliferation.

Male Fischer-344 rats were administered European High Test gasoline (EHT) (50-500 mg/kg), PS-6 unleaded gasoline (UG) (16-500 mg/kg) or 2,2,4-trimethylpentane (TMP) (0.95-30 mg/kg) by gavage for ten consecutive days. To measure cell replication, rats were exposed to [3H]thymidine continuously over the last 7 days of the exposure period. Twenty-four hours after the final dose, protein droplet (PD) accumulation, alpha 2u-globulin (alpha 2u) concentration and the nuclear labeling index (LI), as a measure of cell replication, were measured in the kidneys of control and treated rats. Dose-related increases in PD, alpha 2u and cell replication were detected in the kidneys of rats treated with either gasoline mixture or TMP. The accumulation of PD and the increase in alpha 2u was greater in the kidneys of UG- and TMP-treated rats than in the kidneys of rats treated with EHT. These differences were attributed to the higher composition of branched hydrocarbons in UG, which have been shown to be the biologically active components for these endpoints. The extent of renal cell proliferation was similar in both EHT-, UG- and TMP-treated rats. This suggests that other components besides the branched hydrocarbons are responsible for the increased renal cell replication in EHT-treated rats.

Administration, Oral↗
PubMed1992

The changes of gasoline compounds in blood in a case of gasoline intoxication.

A 44 year-old man, found in his gasoline vapor filled car, died of multiple organ failure on d 9. Blood samples from d 2-7 were analyzed by gas chromatography/mass spectrometry. The estimated half-lives of gasoline, toluene, ethylbenzene, m,p-xylene, and o-xylene were 16.9, 21.4, 27.5, 32.8, and 25.8 h respectively. The estimated initial gasoline concentration in blood was 247 micrograms/ml.

Acidosis↗
PubMed1988

Rapid postexposure decay of alpha 2u-globulin and hyaline droplets in the kidneys of gasoline-treated male rats.

Unleaded gasoline induces nephropathy, characterized by rapid accumulation of hyaline (protein resorption) droplets in epithelial cells of the renal proximal convoluted tubules, only in male rats. The hepatic synthesis of the male rat-specific protein alpha 2u-globulin, a constituent of renal hyaline droplets, is unaltered by gasoline treatment (Olson et al., 1987). Renal alpha 2u-globulin content increased to 210% of control within 18 h of a single oral dose of gasoline (2.0 ml/kg); maximal levels (320% of control) were attained following gasoline administration for 3 d. Increases in renal alpha 2u-globulin caused by gasoline were accompanied by concurrent proliferation of hyaline droplets. However, within 3 d of terminating gasoline administration renal alpha 2u-globulin content decreased to the same level as that in unexposed rats, although renal hyaline droplet number returned to pretreatment levels somewhat more slowly. The conjoint effect of postexposure recovery and estradiol (an inhibitor of hepatic alpha 2u-globulin synthesis) administration was also determined in male rats. On postexposure d 3, 6, and 9, estradiol treatment (1 mg/kg, sc, 4 d, starting on d 9 of gasoline treatment) decreased renal alpha 2u-globulin content to 75%, 59%, and 48%, respectively, of that in rats allowed to recover from gasoline with no hormone treatment. Hepatic alpha 2u-globulin content in estradiol-treated rats was decreased by 74%, 97%, and 96% at the same intervals. Estradiol treatment during recovery from gasoline also appeared to increase the removal of accumulated hyaline droplets from the renal cortex. Thus, accumulation of alpha 2u-globulin-containing hyaline droplets after subacute exposure of male rats to gasoline is rapidly reversible, dependent on continuous exposure to gasoline and maintenance of the normal rate of hepatic alpha 2u-globulin synthesis. These results emphasize the dynamic state of renal cortical hyaline droplets and suggest strongly that gasoline hydrocarbons cause hyaline droplet accumulation by prolonging the half-time of degradation of alpha 2u-globulin.

Alpha-Globulins↗
PubMedDate not supplied

Individual and population exposures to gasoline.

Gasoline is a complex mixture of many constituents in varying proportions. Not only does the composition of whole gasoline vary from company to company and season to season, but it changes over time. The composition of gasoline vapors is dominated by volatile compounds, while "gasoline" in groundwater consists mainly of water-soluble constituents. Hydrocarbons, including alkanes, alkenes, and aromatics, make up the large majority of gasoline, but other substances, such as alcohols, ethers, and additives, may also be present. Given this inability to define "gasoline,h' exposures to individual chemicals or groups of chemicals must be defined in a meaningful exposure assessment. An estimated 111 million people are currently exposed to gasoline constituents in the course of refueling at self-service gasoline stations. Refueling requires only a few minutes per week, accruing to about 100 min per year. During that time, concentrations in air of total hydrocarbons typically fall in the range 20-200 parts per million by volume (ppmV). Concentrations of the aromatic compounds benzene, toluene, and xylene rarely exceed 1 ppmV. Some liquid gasoline is also released, generally as drops less than 0.1 g each, but with enough larger spills to raise the average loss per gallon dispensed to 0.23 g for stations with conventional nozzles and 0.14 g per refueling for stations with vapor recovery nozzles (Stage II controls). Some skin exposure may occur from these spills but the exposure has not been quantified. Two major types of vehicular emissions have been studied. Evaporative emissions include emissions while the vehicle is driven (running losses), emissions after the engine has been shut off but is still warm (hot soak), and emissions during other standing periods (diurnal) emissions. These evaporative emissions are dominated by the more volatile gasoline components. Tailpipe emissions include some unreacted gasoline constituents as well as products of combustion (including chemicals identical to some of the original constituents of the gasoline) and a variety of hydrocarbons and related compounds. Running losses are reported to fall in the range of 0.2 to 2.8 g of total hydrocarbons per mile driven, while benzene evaporative emissions range from 0.002 to 0.007 g/mile. Benzene levels inside travelling vehicles have been reported to average about 13 ppbV in Los Angeles. Tailpipe emissions amount to 0.3 to 1.0 g/mile of total hydrocarbons; emissions of benzene, polycylic aromatic hydrocarbons, and 1,3-butadiene have been reported to range from 0.015 to 0.04 g/mile, 0.00025 to 0.00046 g/mile, and 0.001 to 0.005 g/mile, respectively.(ABSTRACT TRUNCATED AT 400 WORDS)

Environmental Exposure↗
PubMed1989

Health effects of gasoline refueling vapors and measured exposures at service stations.

Liquid gasoline is a complex mixture of at least 150 hydrocarbons with about 60-70% alkanes (paraffins), 25-30% aromatics, and 6-9% alkenes. In order to evaluate the potential for health effects from inhaling gasoline vapors, it is essential to understand the major differences in the composition of vapors versus liquid gasoline. The small chain, low carbon-numbered components are more volatile and thus in higher percentages in the vapor phase than the larger and heavier molecules. It is noteworthy that the concentrations of aromatics (the more toxic of the gasoline components), are depleted to about 2% in the vapor phase, with the light paraffins (the less toxic) enriched to about 90%. Actual measurements of vapor exposure at service stations confirm that the vapor composition is primarily to low weight alkanes although benzene is also emitted and represents the chemical of greatest concern. A perceived health concern from inhaling gasoline vapors is the potential for carcinogenicity based on the induction of kidney tumors in male rats and liver tumors in female mice exposed to wholly-vaporized gasoline. However, the results of the animal studies are of questionable relevance for human risk assessment due to the unique mechanism operative only in the male rat and since the exposure was to wholly-vaporized gasoline rather than the gasoline vapor mixture to which humans are exposed. Recent research supports the hypothesis that branched-chain-alkanes bind to a globulin specific to make rats, alpha 2-u-globulin. The protein complex can not be degraded in the usual manner so that protein accumulation occurs in renal cells, leading to cytotoxicity, death, proliferation, and with prolonged exposure, kidney cancer. The results of epidemiology studies fail to link an increase in cancer to exposure to gasoline vapors.

Air Pollutants↗
PubMed1977

Response of microorganisms to an accidental gasoline spillage in an arctic freshwater ecosystem.

The response of microorganisms to an accidental spillage of 55,000 gallons of leaded gasoline into an Arctic freshwater lake was studied. Shifts in microbial populations were detected after the spillage, reflecting the migration pattern of the gasoline, enrichment for hydrocarbon utilizers, and selection for leaded-gasoline-tolerant microorganisms. Ratios of gasoline-tolerant/utilizing heterotrophs to "total" heterotrophs were found to be a sensitive indicator of the degree of hydrocarbon contamination. Respiration rates were elevated in the highly contaminated area, but did not reflect differences between moderately and lightly contaminated areas. Hydrocarbon biodegradation potential experiments showed that indigenous microorganisms could extensively convert hydrocarbons to CO(2). In situ measurement of gasoline degradation showed that, if untreated, sediment samples retained significant amounts of gasoline hydrocarbons including "volatile components" at the time the lake froze for the winter. Nutrient addition and bacterial inoculation resulted in enhanced biodegradative losses, significantly reducing the amount of residual hydrocarbons. Enhanced biodegradation, however, resulted in the appearance of compounds not detected in the gasoline. Since the contaminated lake serves as a drinking water supply, treatment to enhance microbial removal of much of the remaining gasoline still may be advisable.

Alaska↗
PubMed1991

Benzene pollution from gasoline usage.

Local gasolines contain benzene ranging from 1.8 to 3.7% and their use can lead to significant exposure to benzene. Gasoline station attendants were found to be exposed to short-term exposure levels (STEL) of 0.064-179 ppm. Their 8-h time-weighted averaged (TWA) exposure ranged from 0.028 to 0.71 ppm. For motorcar service mechanics, TWA exposure levels ranged from 0.014 to 1.7 ppm. The exposure of drivers of gasoline delivery tankers ranged from 0.08 to 2.37 ppm for personal TWA exposure over the whole workshift. For local people not occupationally exposed to gasoline or other benzene-containing volatile chemicals, exposure from the ambient environment ranged from 0.0023 to 0.027 ppm. Gasoline usage also contributed to the contamination of surface water with benzene. Benzene levels in water samples taken from drains leading from gasoline stations were between 1.1 and 40.4 micrograms l-1.

Air Pollution↗
PubMed1989

Carcinogenic potential of gasoline and diesel engine oils.

Used gasoline engine oils are carcinogenic in mouse skin and mutagenic in Salmonella. The toxicity of fresh gasoline engine oils and that of fresh and used diesel engine oils are less well defined. The present studies examined the dermal carcinogenic potential of a series of fresh and used oils from both gasoline and diesel engines. The used oils represented a variety of operating conditions. The objective of the study was to assess the potential carcinogenic hazards associated with exposure to these materials. The majority of the used gasoline engine oils tested were carcinogenic although one oil, collected after a relatively short drainage interval, was inactive in the dermal carcinogenesis bioassay. Additionally, polycyclic aromatic hydrocarbon (PAH) concentrations were elevated in the used oils in comparison to the fresh oils. The fresh gasoline engine oils and both the fresh and used diesel engine oil samples were noncarcinogenic, and there was little evidence of elevated PAH levels in the used diesel engine oils. The carcinogenic potency of used oils from gasoline engines was related to drainage interval, but other factors such as contribution of the fuel due to blowby and driving cycle may also have been important. The used diesel engine oils were not carcinogenic even after extended use.

Animals↗
PubMed1992

Dangerous and cancer-causing properties of products and chemicals in the oil refining and petrochemical industry. VIII. Health effects of motor fuels: carcinogenicity of gasoline--scientific update.

1. Significant increases in tumors of kidney, liver, and other tissues and organs following exposure to gasoline provide sufficient evidence of carcinogenicity. 2. Benzene, a significant component of gasoline, has been established without question as a human carcinogen by IARC, EPA, and WHO. 3. 1,3-Butadiene, a component of gasoline, is a powerful carcinogen in both animals and humans. 4. Sufficient evidence for the carcinogenicity of alkyl benzenes, very significant components of gasoline, has also been established. 5. Human epidemiologic studies show important increases in cancers of the kidney, stomach, brain, pancreas, prostate, lung, and skin as well as hematopoietic and lymphatic leukemias as a result of exposure to gasoline, its components, and its vapors. 6. Stage 2 controls are being implemented to reduce exposure of the human population to gasoline vapors.

Animals↗
PubMed1989

Phagolysosomal alterations induced by unleaded gasoline in epithelial cells of the proximal convoluted tubules of male rats: effect of dose and treatment duration.

Short-term oral administration of unleaded gasoline to male rats reproduces the accumulation of phagolysosomes (hyaline droplets) in epithelial cells of the renal proximal convoluted tubules (PCT) observed following long-term inhalation of wholly volatilized gasoline. Phagolysosomes are partially composed of alpha 2u-globulin, a low-molecular-weight protein, unique to male rats. In this study, dose-dependent and chronologic alterations of phagolysosomes caused by gasoline were observed by transmission electron microscopy. Exposure to commercially available unleaded gasoline (0.4-2.0 ml/kg, po, once daily, 9 d) increased the number and size of phagolysosomes in epithelial cells of the PCT in male rat kidney. However, administration of 0.04 ml gasoline/kg or less was ineffective in inducing phagolysosomal accumulation. Subcellular analysis revealed that many of the phagolysosomes observed in treated rats (doses greater than 0.4 ml/kg) were angular and had cross-sectional diameters varying from 0.5 to 9 microns; in controls the majority of phagolysosomes were round and their diameter varied from 0.5 to 2.5 microns. Treatment of male rats with gasoline (2.0 ml/kg body weight, po, 1-9 d) caused a progressive increase in the number and size of phagolysosomes in PCT epithelial cells dependent on treatment duration. Alterations in phagolysosomal morphology and quantity occurred within 20 h following a single dose of gasoline, emphasizing that the process of phagolysosome accumulation is a dynamic phenomenon. Many of the enlarged phagolysosomes contained a condensed, crystalline core of greater electron density than the surrounding matrix. Furthermore, the rapid increase in abnormal, condensed contents in the phagolysosomes may indicate that a derangement of renal protein catabolism is the primary mechanism by which fuel hydrocarbons cause hyaline droplet nephropathy in male rats.

Animals↗
PubMed1992

[The carcinogenicity of gasoline (review of the literature)].

In accord with new findings, the gasoline is no more believed to be free of cancerogenic risk. Renal tumours in male rats and those of liver in murine females had been described also after inhalatory exposure to unleaded gasoline. A reliable epidemiological study in occupationally gasoline exposed humans is still not available (higher rate of tumours in workers of chemical petrol processing industry due to the influence of gasoline appears to be an indirect proof, because apart from gasoline also other substances are involved simultaneously). With regard to a mechanism of action, those first published have been the negative results of testing for chromosomal abnormalities and bacterial genetic mutations. However, the mutagenicity was proved further on molecular level with the use of appropriate tests (e. g. induction of DNA repair synthesis). Certain authors ascribe more importance to the promotional rather than initiational effect of gasoline. However, the former is not accentuated by the IARC. Further studies should be predominantly based on molecular genetic approaches and epidemiological studies.

Animals↗
PubMed1988

Antipyrine and metronidazole metabolism during occupational exposure to gasoline.

Antipyrine and metronidazole clearance was measured in 18 fuel-filling attendants by the single-sample method while the attendants were being exposed occupationally to gasoline; the measurements were repeated after 2-4 weeks with no exposure. Eighteen office workers were investigated simultaneously. The median concentration of gasoline in the breathing zone of the fuel-filling attendants during filling and cleaning operations was 270 mgm-3 (range 18-1758 mgm-3). Antipyrine clearance was 18% higher during exposure to gasoline than after 2-4 weeks of vacation (P less than 0.01), while antipyrine clearance was unchanged in the office workers. No change was found in metronidazole clearance in either group. Antipyrine clearance was on average 26% higher in the smokers than in the nonsmokers (P less than 0.05), while metronidazole clearance was similar in smokers and nonsmokers. We conclude that gasoline is an inducer of antipyrine elimination, with no impact on metronidazole elimination. This indicates that gasoline has a differential inducing effect on the hepatic drug metabolizing enzymes of man.

Adult↗
PubMed1987

Accumulation of alpha 2u-globulin in the renal proximal tubules of male rats exposed to unleaded gasoline.

Saturated branched-chain aliphatic hydrocarbons, found in motor fuels, induce nephrotoxicity in male rats. Treatment of male rats with unleaded gasoline (0.04-2.0 ml/kg body wt, po) for 9 days increased markedly the number and size of hyaline (protein resorption) droplets in epithelial cells of the renal proximal convoluted tubules (PCT) and enhanced cellular exfoliation at high dose levels. No other treatment-related pathological effects were observed in the glomeruli, distal tubules, or medulla. The renal content of alpha 2u-globulin, a major urinary protein of male rats, was increased maximally by about 4.4-fold after gasoline administration (1.0 ml/kg, po, 9 days); no further increase was observed at higher doses. Immunoperoxidase staining of kidney tissue sections for alpha 2u-globulin revealed large accumulations of antigen localized in many of the PCT epithelial cells which contained hyaline droplets. The hepatic content of alpha 2u-globulin and its mRNA were not altered by gasoline administration. These data show, for the first time, that alpha 2u-globulin is accumulated in the kidneys of gasoline-intoxicated male rats and sequestered specifically in some of the hyaline droplets characteristic of gasoline-induced nephropathy. A hydrocarbon-induced defect in the renal lysosomal degradation of low-molecular-weight urinary proteins, rather than increased synthesis of these proteins, appears to cause hyaline droplet accumulation.

Administration, Oral↗
PubMed1988

Leupeptin-mediated alteration of renal phagolysosomes: similarity to hyaline droplet nephropathy of male rats exposed to unleaded gasoline.

alpha 2u-Globulin, a protein of hepatic origin found in the urine of male rats, is accumulated in the kidney cortex during exposure to unleaded gasoline and has been implicated in the development of fuel hydrocarbon-induced nephropathy and renal neoplasia. The principal morphological feature of gasoline-induced nephropathy is accumulation of hyaline droplets (enlarged secondary lysosomes or phagolysosomes) in epithelial cells of the proximal convoluted tubule S1 and S2 segments. Inhibition of cathepsin B (a major lysosomal peptidase) by treatment of male rats with leupeptin causes rapid accumulation of phagolysosomes and alpha 2u-globulin in the kidney very similar to gasoline exposure. Further, the renal cortical subcellular distribution of alpha 2u-globulin, determined with an electron microscopic immunochemical method, is almost totally confined to phagolysosomes following administration of either gasoline or leupeptin. These results, taken together, indicate that the mechanism of nephrotoxicity of gasoline involves inhibition of renal phagolysosomal proteolysis.

Alpha-Globulins↗
PubMed1992

Co-exposure to gasoline vapor decreases benzene metabolism in Fischer-344 rats.

The metabolic interactions of benzene and gasoline vapor were investigated in male Fischer-344 rats. A closed chamber gas-uptake exposure system was used to obtain inhalation uptake curves for benzene alone and benzene in the presence of gasoline vapor. Exposure to benzene as a component of gasoline vapor resulted in a decrease of benzene metabolism. A physiologically based pharmacokinetic model of benzene metabolism was used to quantitatively determine the extent of the inhibitory effect of gasoline vapor on benzene metabolism. This observed inhibitory effect cannot be accounted for by the presence of toluene in gasoline vapor.

Animals↗
PubMedDate not supplied

Exposure to emissions from gasoline within automobile cabins.

Gasoline is emitted from automobiles as uncombusted fuel and via evaporation. Volatile organic compounds (VOC) from gasoline are at higher levels in roadway air than in the surrounding ambient atmosphere and penetrate into automobile cabins, thereby exposing commuters to higher levels than they would experience in other microenvironments. Measurements of VOC concentrations and carbon monoxide were made within automobiles during idling, while driving on a suburban route in New Jersey, and on a commute to New York City. Concentrations of VOC from gasoline were determined to be elevated above the ambient background levels in all microenvironments while VOC without a gasoline source were not. The variability of VOC concentrations with location within the automobile was determined to be smaller than inter-day variability during idling studies. VOC and carbon monoxide levels within the automobile cabin differed among the different routes examined. The levels were related to traffic density and were inversely related to driving speed and wind speed. Overall, daily VOC exposure for gasoline-derived compounds during winter commuting in New Jersey was estimated to range between 5 and 20% and constituted between 15 and 40% of an individual's daily exposure based on comparison to urban and suburban settings, respectively. VOC exposure during commuting in Southern California was estimated to range between 15 and 60%.

Air↗