Biomedical subjects

Q Bui

Publications and source records attributed to Q Bui.

11 recordsLinked to original sources

PubMed2000

Toxicity evaluation of petroleum blending streams: inhalation subchronic toxicity/neurotoxicity study of a light catalytic reformed naphtha distillate in rats.

A 13-wk whole-body inhalation study was conducted with Sprague-Dawley CD rats (16/sex/group) exposed to a light catalytic reformed naphtha distillate (LCRN-D, CAS number 64741-63-5) at target concentrations of 0, 750, 2500, and 7500 ppm for 6 h/d, 5 d/wk. Sixteen rats per sex in the control and high-dose groups were maintained after final exposure for a 4-wk recovery period. The highest exposure concentration was 75% of the lower explosive limit. Standard parameters of subchronic toxicity were measured throughout the study; at necropsy, organs were weighed and tissues processed for microscopic evaluation. Neurotoxicity evaluations consisted of motor activity (MA) and a functional operational battery (FOB) measured pretest, throughout exposure and after the recovery period. Neuropathology was evaluated at termination. No test-related mortality or effects on physical signs, body weight, food consumption, or clinical chemistry were observed. In males exposed to 7500-ppm LCRN-D, a statistically significant decrease in white blood cell counts and lymphocyte counts was observed at the termination of exposure that was not present in animals after the 4-wk recovery period. However, mean corpuscular volume was slightly decreased in high-dose males after the recovery period. Statistically significant increases in kidney weights relative to body weights in 7500-ppm male rats correlated with microscopically observed hyaline droplet formation and renal tubule dilation, indicative of light hydrocarbon nephropathy, a condition in male rats that is not toxicologically significant for humans. Statistically significant decrease in absolute and relative spleen weights in 7500-ppm male rats correlated with decreases in hematologic parameters but had no microscopic correlate and was not observed in animals after 4 wk of recovery. This mild, reversible effect in white blood cell populations may relate to the presence of aromatics in the distillate. The only effect of LCRN-D on neurobehavioral parameters was significantly higher motor activity counts among high-dose (7500 ppm) males after the 4-wk recovery period, suggesting a possible delayed effect of LCRN-D. However, there was no evidence of hyperactivity or abnormal behavior from the functional observational battery evaluations, and there were no microscopic changes in neural tissue to support this observation. The no-observed-adverse-effects level (NOAEL) for LCRN-D was 2500 ppm for both subchronic toxicity and neurotoxicity. The no-observed-effects level (NOEL) was 750 ppm.

Administration, Inhalation↗

PubMed2000

Toxicity evaluation of petroleum blending streams: reproductive and developmental effects of light catalytic reformed naphtha distillate in rats.

A distillate of light catalytic reformed naphtha (CAS number 64741-63-5, LCRN-D) administered by inhalation was tested for reproductive and developmental toxicity in Sprague-Dawley rats, following a modified OECD Guideline 421, Reproductive/Developmental Toxicity Screening protocol. LCRN-D was administered as a vapor, 6 h/d, 7 d/wk at target concentrations of 0, 750, 2500 or 7500 ppm to female rats for approximately 6 wk from 2 wk prior to mating, during mating through gestational d 19, and to males beginning 2 wk prior to mating for approximately 7 consecutive weeks. Dams and litters were sacrificed on postnatal d 4 and males were sacrificed within the week after the last litter was necropsied. Parental systemic effects observed at the 7500 ppm exposure level included slightly lower body weights for males throughout the study. Increased kidney to body weight and increased liver to body weight ratio in male rats exposed to 7500 ppm LCRN-D may be related to slightly lower final mean body weights. Body and organ weight data for female rats in all exposure groups were comparable to controls. No test-material-related microscopic changes were observed in the reproductive organs or nasal turbinate tissue of either sex. Reproductive performance was unaffected by exposure to LCRN-D. The mating and fertility indices were 100% in all groups. There were no significant exposure-related differences in implantation sites or live pups per litter, and no gross abnormalities were observed in pups from treated dams. Pups born from LCRN-D-exposed dams showed comparable body weights and weight gain to control pups. The viability index on postpartum d 4 was > or =97%. Under conditions of this study, the no-observed-adverse-effect level (NOAEL) for exposure to light catalytic reformed naphtha distillate for parental effects was 2500 ppm and the NOAEL for reproductive and developmental toxicity was 7500 ppm.

Alkanes↗

PubMed1999

Toxicity evaluation of petroleum blending streams: reproductive and developmental effects of light catalytic cracked naphtha distillate in rats.

A distillate of light catalytic cracked naphtha (CAS number 64741-55-5, LCCN-D), administered by inhalation, was tested for reproductive and developmental toxicity in Sprague-Dawley rats, following a modified OECD Guideline 421, Reproductive/Developmental Toxicity Screening Protocol. LCCN-D was administered as a vapor, 6 h/d, 7 d/wk at target concentrations of 0, 750, 2500 or 7500 ppm to female rats for approximately 7 wk from 2 wk prior to mating, during mating through gestational d 19, and to males beginning 2 wk prior to mating for 8 consecutive weeks. Dams and litters were sacrificed on postnatal d 4, and males were sacrificed within the following week. Parental systemic effects observed at the 7500 ppm exposure level were increased kidney weights and relative liver weights in males and increased spleen weights in high-dose females. Livers and spleens from rats in the high-dose group were normal in appearance at necropsy. IncreaSed kidney weights in high-dose males were indicative of male-rat-specific light hydrocarbon nephropathy. No test-related microscopic changes were observed in the reproductive organs or nasal turbinate tissues of either sex. Reproductive performance was unaffected by treatment with LCCN-D. Fertility index was > or =90% in all dose groups. There were no exposure-related differences in implantation sites and live pups per litter, and no gross abnormalities were observed. Pups born from treated dams showed comparable body weights and weight gains to controls. The viability index on postpartum d 4 was > or =97%; the high-dose group had more male than female pups at birth and at d 4 postpartum. Under the conditions of this study, the no-observable-adverse-effect level (NOAEL) for exposure to light catalytic cracked naphtha distillate for parental toxicity was 2500 ppm and the NOAEL for reproductive performance and developmental toxicity was 7500 ppm.

Alkanes↗

PubMed1999

Survey of mammographic cassette light output.

The purpose of the present paper was to assess the variation in light output from clinical mammographic screens, particularly in relationship to age and radiographic usage. The light output from 156 mammographic cassettes from 17 clinical centres was measured on site using a novel light detector. Survey information on cassette age and usage was collected. Where possible, screen manufacture date was supplied by the vendor. One cassette from each centre was measured at a standard laboratory to allow normalization of all measurements. Three centres were found to have cassettes in clinical use whose light outputs varied by an amount incompatible with current Royal Australasian College of Radiologists (RACR) standards. These centres used cassettes whose ages varied widely. No correlation between light output and radiographic usage was found. Older cassettes were found to have a slight increase in light output. A small reduction of light output was measured between screen regions of high and low radiation exposure histories. Replacement of mammographic screens should not be based on an expectation of light output reduction due to age or usage. Rather, all mammographic screens should be replaced simultaneously as indicated by factors such as failure of screen-film contact or the presence of screen-related image artefacts.

Humans↗

PubMed1998

Toxicity evaluation of petroleum blending streams: inhalation subchronic toxicity/neurotoxicity study of a light alkylate naphtha distillate in rats.

A 13-wk inhalation study was conducted with Sprague-Dawley CD rats (12/sex/group) were exposed by inhalation for 13 weeks to a light alkylate naphtha distillate (LAND-2, C4-C10; average molecular weight 89.2) at actual average concentrations of 0 (room air), 668, 2220, or 6646 ppm, 6 h/d, 5 d/wk; 12 additional rats/sex in the control and high dose groups were held after final exposure for a 4-wk recovery period. The highest exposure concentration was 75% of the lower explosive limit. Standard parameters of subchronic toxicity were measured throughout the study; at necropsy, organs were weighed and tissues processed for microscopic evaluation. Neurotoxicity evaluations consisted of motor activity (MA) and a functional operational battery (FOB) measured pretest, during 5, 9, and 14 wk of the study, and after the 4-wk recovery period. Whole-body perfusion and microscopic examination of selected organs and nervous tissue from the control and high dose rats were conducted at the end of exposure. No test-related mortality or effects on physical signs, body weight, or food consumption were observed. Statistically significant increases in absolute and relative kidney weights in high-exposure males correlated with microscopically observed hyaline droplet formation and renal nephropathy, effects in male rats that are not toxicologically significant for humans. Increased liver weights in both sexes at the highest dose had no microscopic correlate and appeared reversible after the 4-wk recovery period. Exposure to LAND-2 at any dose did not produce neurotoxicity measured by MA, FOB, or neuropathology. The no-observed-effects level (NOEL) for LAND-2 was 2220 ppm for subchronic toxicity and > or =26646 ppm for neurotoxicity.

Administration, Inhalation↗

PubMed1997

Toxicity evaluation of petroleum blending streams: reproductive and developmental effects of hydrodesulfurized kerosine.

Hydrodesulfurized kerosine (HDS kerosine), applied dermally, was tested for reproductive and developmental toxicity in Sprague-Dawley rats, using a modified OECD Guideline 421, Reproductive/Developmental Toxicity Screening Protocol. A preliminary acute dermal irritancy test demonstrated that dilution of HDS kerosine in either a light (100 Saybolt universal seconds, SUS) or moderate viscosity (340 SUS) USP mineral oil reduced irritation of the neat material comparably. Similar dermal absorption was observed in vitro for neat HDS kerosine or diluted in either of the mineral oils. HDS kerosine diluted to 494 (60%), 330 (40%), or 165 (20%) mg/kg/day in Squibb mineral oil (340 SUS) was applied daily at 1 ml/kg to the shaved backs of rats for 7 wk (premating, mating to d 19 of gestation) to females and 8 wk to males. Dams and litters were sacrificed on postpartum d 4 and males were sacrificed within the following week. HDS kerosine produced slight to moderate skin irritation at the highest dose in both sexes but no apparent maternal, reproductive, or developmental toxicity. No clinical signs of toxicity and no effects on body weight, food consumption, or absolute organ weights were observed. Relative kidney weights were heavier in male rats at the high dose. Skin changes were observed microscopically in male rats in all groups and in females at the high dose. No microscopic changes were observed in reproductive organs of parental animals. There were no differences in mean number of corpora lutea, implantation sites, and live pups per litter, and no gross anomalies were observed. Pups born from treated dams showed comparable body weights and weight gains to controls. The viability index on postpartum d 4 was > or = 93%. In conclusion, the no observable adverse effect level (NOAEL) for HDS kerosine for reproductive and developmental toxicity in rats is 494 mg/kg/d.

Administration, Topical↗

PubMed1997

X-ray intensifying screen visible light detection meter.

A light meter has been designed and built for the purpose of measuring the light emitted from an intensifying screen during x-ray irradiation. The meter uses a photodiode detector with a minimal drift amplification system. The meter repeatability was better than 0.5% and was found to be linear. A significant x-ray induced signal was recorded during measurement which needed to be subtracted from readings to deduce the intensification screen light output. The energy response of four screen types was subsequently measured.

Radiometry↗

PubMed1991

Modulation of calcium-activated chloride current via pH-induced changes of calcium channel properties in cone photoreceptors.

The activity of calcium-activated chloride channels is controlled through the complex interaction of cellular mechanisms affecting calcium entry, buffering, and extrusion, and an unknown stoichiometric relation between intracellular Ca concentration and Cl channel activation. Here, we show that calcium-activated chloride current [ICl(Ca)] in cone photoreceptors is also highly sensitive to external pH, being strongly reduced by acidification and enhanced by alkylinization of the bathing medium. We propose that this modulation is accounted for by the pH sensitivity of Ca channel activation and permeation, already well characterized in other cells, which we now extend to cone photoreceptor Ca channels. Acidification of the external medium from a control pH of 7.4 shifts the Ca channel activation range positively by about 10 mV at pH 6.8, reducing the magnitude of calcium current with a consequent reduction of chloride current. Alkylinization shifts the Ca channel activation range negatively by about 8 mV at pH 8 and produces larger calcium currents during step depolarizations that in turn elicit larger chloride tail currents. Modulation of ICl(Ca) by pH suggests other consequences of the pH-induced shift in Ca channel gating, for one, modification of Ca-dependent transmitter release, which could be especially significant in photoreceptors where the cell's operating voltage range overlaps only the lower end of the Ca channel activation range.

Ambystoma↗

PubMed1988

Identification of microsomal, organic hydroperoxide-dependent catechol estrogen formation: comparison with NADPH-dependent mechanism.

Exogenous aromatic polycyclic hydrocarbons, notably benzo[a]pyrene, can be metabolized by both NADPH-dependent monooxygenase(s) and an organic hydroperoxide (OHP)-dependent mechanism. To determine whether phenolic estrogens, endogenous aromatic polycyclic hydrocarbons, can also be hydroxylated by these alternative pathways, conversion of estradiol (E2) to 2- and 4-hydroxylated catecholestrogens (2- and 4-OH-CEs) by human placental microsomes was examined under conditions previously shown to support CE formation by NADPH- and OHP-dependent mechanisms. CEs were formed under both conditions. Properties of OHP-dependent activity were similar to CE formation by peroxidases and distinct from the NADPH-dependent monooxygenase. NADPH supported only 2-hydroxylation, whereas cumene hydroperoxide supported 2- and 4-hydroxylation equally. Monooxygenase-mediated activity had characteristics of a high-affinity, low-capacity enzyme system (apparent Km for E2 = 0.3 microM, and Vmax = 31 pmol/mg protein/30 min), whereas peroxidatic activity had properties of low affinity and high capacity (apparent Km for E2 = 55 microM, Vmax = 666 pmol/mg protein/10 min). The requirement of peroxidatic activity for oxidizing co-substrate could be met by OHPs but not by H2O2. Peroxidatic CE formation could have special functional significance for physiological and pathological consequences of estrogen action since it generates 4-OH-CEs which are both effective catechols and potent, long-acting estrogens. Moreover, it could provide a link through co-oxygenation between estrogens and diverse cellular mechanisms involving generation of OHPs.

Carbon Dioxide↗

PubMedDate not supplied

Developmental toxicity evaluation of unleaded gasoline vapor in the rat.

To evaluate the potential of unleaded gasoline vapor for developmental toxicity, a sample was prepared by slowly heating API 94-02 (1990 industry average gasoline) and condensing the vapor. The composition of this vapor condensate, which comprises 10.4% by volume of the starting gasoline, is representative of real-world exposure to gasoline vapor encountered at service stations and other occupational settings and consists primarily of volatile short chain (C4-C6) aliphatic hydrocarbons (i.e. paraffins) with small amounts of cycloparaffins and aromatic hydrocarbons. A preliminary study in rats and mice resulted in no developmental toxicity in either species. However, a slight reduction in maternal body weight gain in rats led to the selection of rats for this guideline study. Groups of pregnant rats (n = 24/group) were exposed to unleaded gasoline vapor at concentrations of 0, 1000, 3000, or 9000 (75% lower explosive limit) ppm equivalent to 0, 2653, 7960, or 23,900 mg/m3, for 6 h/day on gestation days 6-19. All rats were sacrificed on gestation day 20. No maternal toxicity was observed. Developmentally, there were no differences between treated and control groups in malformations, total variations, resorptions, fetal body weight, or viability. The maternal and developmental NOAEL is 9000 ppm. Under conditions of this study, unleaded gasoline vapors did not produce evidence of developmental toxicity.

Administration, Inhalation↗

PubMedDate not supplied

Toxicity evaluation of petroleum blending streams: inhalation subchronic toxicity/neurotoxicity study of a light catalytic cracked naphtha distillate in rats.

A 15-week, whole-body inhalation study of the vapors of a distillate (LCCN-D) of light catalytic cracked naphtha (CAS no. 64741-55-5, LCCN) was conducted with Sprague-Dawley rats. Target exposure concentrations were 0, 750, 2500, and 7500 ppm for 6 hours/day, 5 days/week. Over the course of the study, animals received at least 65 exposures. For a portion of the control and 7500-ppm groups, a 4-week postexposure period was included in the study. Subchronic toxicity was evaluated using standard parameters. During life, neurotoxicity was evaluated by motor activity assessment and a functional observational battery. Selected tissues from animals in all exposure groups were examined microscopically. Neuropathologic examination of selected neuronal tissues from animals in the control and high-exposure groups was also conducted. No compound-related effects were seen on survival, clinical chemistry, food consumption, or physical signs. No evidence of neurotoxicity was seen at any exposure level. Slight decreases in hematocrit and hemoglobin concentrations were seen in male rats at the end of exposure to 7500 ppm LCCN-D. However, values were within normal physiological ranges and recovery occurred. Slight decreases in mean body weights and body weight gain were observed in high-exposure females during the first 7 weeks of exposure, but this decrease was not seen during the second half of the study. Male rat nephropathy involving hyaline droplet formation and alpha-2micro-globulin accumulation was seen in mid- and high-exposure males, an effect not relevant to humans. The incidence and severity of goblet cell hypertrophy/hyperplasia and respiratory epithelium hyperplasia in nasoturbinal tissues were greater in high-exposure animals, but recovery occurred. None of the effects observed were considered toxicologically significant. The no-observable-adverse-effect level (NOAEL) for subchronic and neurotoxicity of LCCN-D was > or = 7500 ppm.

Alkanes↗