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Biomedical subjects

H K Hudnell

Publications and source records attributed to H K Hudnell.

22 records · Page 2Linked to original sources
PubMedDate not supplied

Time course of sensory eye irritation in humans exposed to N-butanol and 1-octene.

In this study, we investigated the time course effect of sensory eye irritation in 16 subjects exposed (i.e., eye only) to n-butanol and 1-octene. Half the subjects were exposed to n-butanol, and the remaining subjects were exposed to 1-octene. Each subject was studied on 5 different days; during each day each subject was exposed in three runs (i.e., run 1, run 2, and run 3) to a constant concentration of either n-butanol or 1-octene. We performed run 1 and run 3, both of which lasted 15 min each, to evaluate persistence in "sensitization." We performed run 2, which lasted 60 min, to study the time course of sensory irritation. Ratings of ocular irritation intensity were obtained continuously during all three runs. The exposure concentrations for n-butanol were 0 mg/m3, 300 mg/m3, 900 mg/m3, and 3 000 mg/m3, and the exposure concentrations for 1-octene were 0 mg/m3, 6 000 mg/m3, 10 400 mg/m3, and 18 000 mg/m3. During run 2, we observed a slight increase in perceived eye irritation intensity for the lower concentrations of 1-octene and for all exposure concentrations of n-butanol. However, the threshold for irritation was clearly exceeded for only the 1-octene 10 400-mg/m3 and 18 000-mg/m3 exposures. During these two exposures, the response increased 10-fold following 20-40 min of exposure during run 2, after which the response remained constant. We investigated the existence of persistence in "sensitization" by comparing intensity of responses between run 1 and run 3. Persistence in "sensitization" was apparent for only the 1-octene exposure.

1-Butanol↗
PubMedDate not supplied

Effects from environmental Mn exposures: a review of the evidence from non-occupational exposure studies.

OBJECTIVE: The risk posed to human health by environmental manganese exposure is unknown. Occupational-exposure outcomes may not extrapolate to environmental exposures due to the healthy worker effect and differences in dosage parameters which may affect the biological response. This paper attempts to combine the existing literature on non-occupational Mn exposures with results from our current study in SW Quebec on environmental Mn exposure (Mergler et al., this issue) within the framework of a biologically-based, dose-response (BBDR) model. BBDR MODEL: The basic BBDR model consists of seven stages relating exposure to health effects. The stages are: 1) sources, 2) applied dose, 3) absorbed dose, 4) target-site dose, 5) toxic event, 6) measurable change, and 7) health outcome. RESULTS: Several air monitoring programs, such as the PTEAM study (Riverside, CA, 1990, mean PM10 Mn outdoor-airborne 24 h average = 0.045 microgram/m3), provided data relevant to the estimation of Mn applied dose, but did not include measures of body burden. Data from the SW Quebec study showed a mean total-particulate airborne Mn concentration of 0.022 microgram/m3 with a range of 0.009 to 0.035 microgram/m3 across four sampling sites, whereas the EPA reference concentration (RfC) is 0.05 microgram/m3. EPA has considered tap water levels to be safe below 200 micrograms/l Mn, and mean Mn tap-water (MnW) level in the participants' homes was 6.38 +/- 11.95 micrograms/l with a range from 0.1 to 158.9 micrograms/l Mn. A previous study of MnW exposure in Greece reported Mn levels in areas with low, medium and high MnW ranging from 4 to 2,300 micrograms/l and a significant association with Mn in hair but not Mn in blood (MnB). The mean absorbed dose of the SW Quebec study participants, as indicated by MnB, was 7.5 +/- 2.3 micrograms/l with a range of 2.5 to 15.9 micrograms/l. Our study and others on environmental Mn exposure did not provide an estimate of target-site dose. However, a significant correlation (r = 0.65) between MnB and signal intensity in T1-weighted MRI images has been reported in liver-disease patients with Parkinson-like signs who had MnB levels as low as 6.6 micrograms/l. Only animal and in vitro studies have provided evidence on the mechanisms of toxicity caused by Mn in the CNS. Several studies reported measurable changes in endpoints suggestive of a Parkinson-like syndrome in subjects with MnB levels ranging from 7.5 to 25.0 micrograms/l. Among other effects on neurobehavioral function observed in the current study was a significant relationship between MnB and the direction and speed of body-sway in men. The effects observed in these participants are sub-clinical and no health outcomes have been diagnosed. However, the Parkinson's disease incidence in the study area was previously reported to be 2-5 times higher than in the rest of Quebec, and several studies indicate that 25-35% of idiopathic Parkinson disease diagnoses are incorrect. Our study, the Greek study, and some clinical studies suggest that the risk of a Parkinson-like syndrome diagnosis may increase with continued Mn exposure and aging. CONCLUSION: The limited data available for the BBDR model point to the need for evidence, particularly on relationships between Mn species, exposure route, MnB with chronic environmental exposure, ageing, and susceptibility factors, to improve human-health risk assessments for chronic, environmental Mn exposure.

Dose-Response Relationship, Drug↗
PubMedDate not supplied

Visual contrast sensitivity deficits in Bohemian children.

Visual contrast sensitivity (VCS) tests have been used successfully in medical diagnosis and subclinical neurotoxicity detection. This paper reports VCS measurements in three studies of children in the Czech Republic. Study 1 compared children in standard schools and schools for the learning disabled. Studies 2 and 3 compared children in Teplice, an area in which soft-brown coal combustion produced high levels of pollutants (e.g. Hg, As, SO2, NOx, and aromatic hydrocarbons), with children in areas of low air pollution, Znojmo and/or Prachatice. It was hypothesized that in utero exposure to the combustion products disrupted neurological development (Sram, 1991). The VCS test (Stereo Optical Co.) consisted of circular fields containing sinusoidal gratings at 5 spatial frequencies (1.5-18 cycles/degree) and various levels of contrast. Subjects indicated orientation of the gratings by pointing left, up, or right. Visual acuity and VCS were measured in each eye of 74 children in Study 1,327 second-grade children in Study 2, and 426 fourth-grade children in Study 3. Hair samples were collected in Studies 2 and 3 analyzed for Hg and As content. Children attending schools for the learning disabled scored significantly lower than controls on VCS, whereas visual acuity was normal. The deficit was greatest at mid- to high spatial frequency. In Study 2, significant VCS deficits were seen in exposed second-grade children at low to mid-spatial frequency, even though visual acuity was slightly above control level. Regression analyses showed that VCS had no relationship to As, but a significant negative correlation with hair Hg was observed in the exposed district. However, current Hg levels were higher in Prachatice. VCS deficits were not observed in the fourth-grade students of Teplice in Study 3. The results of Study 1 indicated that behavioral VCS testing in field studies is practical in young, non-English speaking children, and suggested that vision may be compromised in learning-disabled children. Studies 2 and 3 indicated that at these levels, current Hg body-burdens are poor predictors of VCS. If the VCS deficits seen in Study 2 were related to prenatal exposures, the results of Study 3 suggest that they represent a developmental delay. A longitudinal-study design is needed to address this issue.

Child↗