Health assessment of gasoline and fuel oxygenate vapors: subchronic inhalation toxicity.

Sprague Dawley rats were exposed via inhalation to vapor condensates of either gasoline or gasoline combined with various fuel oxygenates to assess whether their use in gasoline influences the hazard of evaporative emissions. Test substances included vapor condensates prepared from an EPA described "baseline gasoline" (BGVC), or gasoline combined with methyl tertiary butyl ether (G/MTBE), ethyl t-butyl ether (G/ETBE), t-amyl methyl ether (G/TAME), diisopropyl ether (G/DIPE), ethanol (G/EtOH), or t-butyl alcohol (G/TBA). Target concentrations were 0, 2000, 10,000 or 20,000mg/m(3) and exposures were for 6h/day, 5days/week for 13weeks. A portion of the animals were maintained for a four week recovery period to determine the reversibility of potential adverse effects. Increased kidney weight and light hydrocarbon nephropathy (LHN) were observed in treated male rats in all studies which were reversible or nearly reversible after 4weeks recovery. LHN is unique to male rats and is not relevant to human toxicity. The no observed effect level (NOAEL) in all studies was 10,000mg/m(3), except for G/MTBE (<2000) and G/TBA (2000). The results provide evidence that use of the studied oxygenates are unlikely to increase the hazard of evaporative emissions during refueling, compared to those from gasoline alone.

Health assessment of gasoline and fuel oxygenate vapors: reproductive toxicity assessment.

Vapor condensates of baseline gasoline (BGVC), or gasoline-blended with methyl tertiary butyl ether (G/MTBE), ethyl t-butyl ether (G/ETBE), t-amyl methyl ether (G/TAME), diisopropyl ether (G/DIPE), ethanol (G/EtOH), or t-butyl alcohol (G/TBA) were evaluated for reproductive toxicity in rats at target concentrations of 2000, 10,000, or 20,000mg/m(3), 6h/day, 7days/week. BGVC and G/MTBE were assessed over two generations, the others for one generation. BGVC and G/MTBE F1 offspring were evaluated for neuropathology and changes in regional brain glial fibrillary acidic protein content. No neurotoxicity was observed. Male kidney weight was increased consistent with light hydrocarbon nephropathy. In adult rats, decreased body weight gain and increased liver weight were seen. Spleen weight decreased in adults and pups exposed to G/TBA. No pathological changes to reproductive organs occurred in any study. Decreased food consumption was seen in G/TAME lactating females. Transient decreases in G/TAME offspring weights were observed during lactation. Except for a minor increase in time to mating in G/TBA which did not affect other reproductive parameters, there were no adverse reproductive findings. The NOAEL for reproductive and offspring parameters was 20,000mg/m(3) for all vapor condensates except for lower offspring NOAELs of 10,000mg/m(3) for G/TBA and 2000mg/m(3) for G/TAME.

Health assessment of gasoline and fuel oxygenate vapors: developmental toxicity in rats.

Gasoline-vapor condensate (BGVC) or condensed vapors from gasoline blended with methyl t-butyl ether (G/MTBE), ethyl t-butyl ether (G/ETBE), t-amyl methyl ether (G/TAME) diisopropyl ether (G/DIPE), ethanol (G/EtOH), or t-butyl alcohol (G/TBA) were evaluated for developmental toxicity in Sprague-Dawley rats exposed via inhalation on gestation days (GD) 5-20 for 6h/day at levels of 0 (control filtered air), 2000, 10,000, and 20,000mg/m(3). These exposure durations and levels substantially exceed typical consumer exposure during refueling (<1-7mg/m(3), 5min). Dose responsive maternal effects were reduced maternal body weight and/or weight change, and/or reduced food consumption. No significant malformations were seen in any study. Developmental effects occurred at 20,000mg/m(3) of G/TAME (reduced fetal body weight, increased incidence of stunted fetuses), G/TBA (reduced fetal body weight, increased skeletal variants) and G/DIPE (reduced fetal weight) resulting in developmental NOAEL of 10,000mg/m(3) for these materials. Developmental NOAELs for other materials were 20,000mg/m(3) as no developmental toxicity was induced in those studies. Developmental NOAELs were equal to or greater than the concurrent maternal NOAELs which ranged from 2000 to 20,000mg/m(3). There were no clear cut differences in developmental toxicity between vapors of gasoline and gasoline blended with the ether or alcohol oxygenates.

Genetic toxicity of high-boiling petroleum substances.

There are several specific types of high-boiling petroleum substances (HBPS) having final boiling points >343°C), in which genetic toxicity can be related to the content of polycyclic aromatic compounds (PACs), specifically crude oils, gas oils, heavy fuel oils, lubricant base oils, waxes and aromatic extracts. Evaluation of optimized Salmonella tests covering over 250 samples from 43 types of HBPS revealed that gene mutation can be determined for these substances using a protocol optimized for the detection of mutagenic PAC. The outcomes of modified Salmonella assays can be predicted using HBPS compositional information as input to a newly developed statistical model. The general outcome of the optimized Salmonella assay can be predicted for an untested substance based on its Aromatic Ring Class (ARC) profile. Review of the results from numerous cytogenetic tests showed that although a few positive study results have been reported, most HBPS do not produce chromosomal effects when tested in rodent bone marrow assays or in in vitro chromosomal aberration assays. Results of both bacterial and cytogenetic studies can be used to satisfy genetic toxicity endpoints for the HBPS category substances.

The development of statistical models to determine the relationship between aromatic-ring class profile and repeat-dose and developmental toxicities of high-boiling petroleum substances.

The repeat-dose and developmental toxicities of certain petroleum refinery streams are related to their polycyclic aromatic compound (PAC) content (Feuston et al., 1994). Building on this foundation, and working within the context of the US EPA High Production Volume (HPV) Chemical Challenge Program, we: (1) characterized relationships between PAC content and repeat-dose and developmental toxicities of high boiling petroleum substances (HBPS), and (2) developed statistical models that can be used to predict critical effects of similar untested substances. Data from 39 dermal toxicity studies of HBPS were used to develop statistical models to predict the dose-response relationships between the weight percent concentration of each of their 1-7 aromatic ring classes and 4 repeat-dose and 3 developmental endpoints (absolute thymus weight, hemoglobin count, platelet count, liver to body weight, live fetus count, fetal weight, and percent resorptions). The correlations between the observed and model-predicted values are >0.90. The predictive ability of the models was tested via a series of evaluation or corroboration methods. As is shown in the paper, using only compositional data of untested HBPS, the models can be used to predict the effect at a given dose or the dose that causes an effect of a stipulated magnitude.

The relationship between developmental toxicity and aromatic-ring class profile of high-boiling petroleum substances.

In response to the US EPA HPV Challenge Program, this study was conducted to: (1) evaluate the relationship between PAC content and the developmental toxicity of high-boiling petroleum substances (HBPS) and (2) develop mathematical models to predict the developmental toxicity of similar untested substances based on their aromatic ring class (ARC) profiles. For this investigation, 68 developmental toxicity studies were reviewed. The ARC models relied on data from 21 rat dermal developmental toxicity studies conducted with similar experimental designs to ensure a consistent data set for comparison. The most sensitive general endpoints of developmental toxicity (i.e., decreased fetal survival and growth) were chosen for modeling. The ARC models demonstrated a strong correlation between the predicted vs. observed values for specific sensitive endpoints of these developmental toxicities (percent resorptions, r=0.99; live fetuses per litter, r=0.98; fetal body weight, r=0.94). Such associations provide a promising approach for predicting the developmental toxicity of untested HBPS. Efforts to corroborate the ARC models using test substances that were not used to build the ARC models produced mixed results, and further development and refinement of the ARC models is recommended before they can be reliably applied to all HBPS.

The relationship between repeat-dose toxicity and aromatic-ring class profile of high-boiling petroleum substances.

A study was undertaken within the context of the U.S. EPA HPV Chemical Challenge Program to (1) characterize relationships between PAC content and repeat-dose toxicities of high-boiling petroleum substances (HBPS) and (2) develop statistical models that could be used to predict the repeat-dose toxicity of similar untested substances. The study evaluated 47 repeat-dose dermal toxicity and 157 chemical compositional studies. The four most sensitive endpoints of repeat-dose toxicity were platelet count, hemoglobin concentration, relative liver weight and thymus weight. Predictive models were developed for the dose-response relationships between the wt.% concentration of each of seven ring classes of aromatic compounds (the "ARC profile") and specific effects, with high correlations (r=0.91-0.94) between the observed and model-predicted data. The development of the mathematical models used to generate the results reported in this study is described by Nicolich et al. (2013). Model-generated dose-response curves permit the prediction of either the effect at a given dose or the dose that causes a given effect. The models generate values that are consistent with other standard measures. The models, using compositional data, can be used for predicting the repeat-dose toxicity of untested HBPS.

Assessing the mammalian toxicity of high-boiling petroleum substances under the rubric of the HPV program.

In 1998, the US EPA announced the HPV Challenge Program, a voluntary chemical data collection effort. The Petroleum HPV Testing Group (PHPVTG(1)) volunteered to provide data on approximately 110 high boiling petroleum substances (HBPS), i.e. substances with final boiling points ≥ approximately 650°F (343°C). These HBPS are substances of unknown and variable composition (UVCBs) that are composed of numerous individual constituents. Toxicity studies have shown that some HBPS can produce systemic (repeat-dose) and developmental effects, and some are mutagenic under in vitro conditions. The papers in this supplement show that these effects are related to the profiles of aromatic constituents in these substances. Further, it is shown that the effects on selected repeat-dose and developmental toxicity endpoints and mutagenic activity in bacterial assays can be predicted from compositional information using models based on the aromatic-ring class profile, "ARC profile" as defined by gas chromatographic separation of the DMSO-soluble fraction of the starting materials. This chromatographic method and the predictive models provide an efficient means of characterizing for screening purposes the potential for repeat-dose, developmental effects and bacterial mutagenicity of HBPS and can reduce the number of animal tests that would be required if these tests were conducted on all 110 HBPS.

Evaluating the male and female reproductive toxicity of high-boiling petroleum substances.

To meet the EPA HPV Chemical Challenge Program requirement for reproductive toxicity data on sponsored high-boiling petroleum substances (HBPS), an analysis was conducted using the results of 39 repeat-dose and 59 developmental rat dermal toxicity studies on HBPS samples spanning the boiling range of the sponsored substances, and the results of three one-generation reproductive toxicity studies on two samples spanning the concentration range of polycyclic aromatic compounds of sponsored substances. The analysis found little evidence of male or female reproductive tract toxicity based on histopathology, reproductive organ weight, and sperm parameters, and no evidence of effects on fertility, while significant developmental toxicity and/or systemic repeat-dose toxicity were frequently observed. Among 14 samples of HBPS tested in both repeat-dose toxicity and developmental toxicity studies, there were no studies in which an adverse reproductive tract finding occurred at a dose lower than that producing developmental toxicity or other adverse effects in repeat-dose toxicity studies. The current analysis supports the hypothesis that effects in developmental and/or repeat-dose toxicity studies of HBPS occur at doses lower than those that might affect fertility in rat one-generation reproductive studies. When adequate developmental and repeat-dose toxicity studies are available, a reproductive toxicity study of HBPS appears unnecessary.

Anion templated surface assembly of a redox-active sensory rotaxane.

Anion templation is used to assemble novel redox-active bis-ferrocene functionalised rotaxane self-assembled monolayers (SAMs) on to gold electrode surfaces; after template removal, the unique SAM rotaxane binding domain is capable of selectively sensing chloride ions electrochemically.