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Biomedical subjects

H Kehrl

Publications and source records attributed to H Kehrl.

6 recordsLinked to original sources

Elderly humans exposed to concentrated air pollution particles have decreased heart rate variability.

Air pollution particles are thought to kill > 500,000 people worldwide each year. The population most at risk appears to be elderly people with respiratory and cardiovascular disease. As yet, no commonly accepted mechanism has been proposed which can explain the cause of these deaths. Heart rate variability (HRV) was assessed in healthy elderly adults between the ages of 60 and 80 who were exposed twice for 2 h: once to clean air and once to concentrated ambient air pollution particles (CAPS). Changes in HRV were measured immediately before, immediately following, and 24 h after exposure. Elderly subjects experienced significant decreases in HRV in both time and frequency domains immediately following exposure. Some of these changes persisted for at least 24 h. These data were compared with HRV data collected from young healthy volunteers exposed to CAPS in a previous study, in which no CAPS-induced changes in HRV were found. These concentrated ambient air pollution particle-induced changes in heart rate variability in a controlled human exposure study extend similar findings reported in recent panel studies and suggest potential mechanisms by which particulate matter may induce adverse cardiovascular events.

Adult↗

Psychoneuroimmunology.

This paper develops hypotheses regarding the interactions among stress, immunity, and chemical sensitivities and gives an overview of the questions and hypotheses generated by a working group exploring the application of psychoneuroimmunology to chemical sensitivities. Consideration is given to prospective longitudinal studies designed to find cases among at-risk exposed populations. Relevant immune parameters to be measured longitudinally and in challenge studies for patients with MCS are discussed. Immune system changes in response to the chronic stress of having MCS and as primary responses to chemical exposure also are considered.

Environment, Controlled↗

Effects of cyclo-oxygenase inhibition on ozone-induced respiratory inflammation and lung function changes.

Inhalation of O3 causes airways neutrophilic inflammation accompanied by other changes including increased levels of cyclo-oxygenase products of arachidonic acid in bronchoalveolar lavage fluid (BALF). Ozone O3 exposure also causes decreased forced vital capacity (FVC) and forced expiratory volume after 1 s (FEV(1)), associated with cough and substernal pain on inspiration, and small increases in specific airway resistance (SRAW). The spirometric decrements are substantially blunted by pretreatment with indomethacin. Since the O3-induced decrement in FVC is due to involuntary inhibition of inspiration, a role for stimulation of nociceptive respiratory tract afferents has been suggested and cyclo-oxygenase products have been hypothesized to mediate this stimulation. However, the relation (if any) between the O3-induced neutrophilic airways inflammation and decreased inspiratory capacity remains unclear. We studied the effects of pharmacologic inhibition of O3-induced spirometric changes on the inflammatory changes. Each of ten healthy men was exposed twice (5-week interval) to 0.4 ppm O3 for 2 h, including 1 h of intermittent exercise (ventilation 601*min(-1)). One-and-a-half hours prior to and midway during each exposure the subject ingested 800 mg and 200 mg, respectively, of the non-steroidal anti-inflammatory drug ibuprofen (IBU), or placebo [PLA (sucrose)], in randomized, double-blind fashion. Spirometry and body plethysmography were performed prior to drug administration, and before and after O3 exposure. Immediately following postexposure testing, fiberoptic bronchoscopy with bronchoalveolar lavage (BAL) was performed. Neither IBU nor PLA administration changed pre-exposure lung function. O3 exposure (with PLA) caused a significant 17 percent mean decrement in FEV(1) (P <0.01) and a 56 percent increase in mean SRAW. Following IBU pretreatment, O3 exposure induced a significantly lesser mean decrement in FEV(1) (7 percent) but still a 50 percent increase in mean SRAW. IBU pretreatment significantly decreased post-O3 BAL levels of prostaglandin E2 (PGE2) by 60.4 percent (P <0.05) and thromboxane B(2) (TxB(2)) by 25.5 percent (P <0.05). Of the proteins, only interleukin-6 was significantly reduced (45 percent, P <0.05) by IBU as compared to PLA pretreatment. As expected, O3 exposure produced neutrophilia in BALF. There was, however, no effect of IBU on this finding. None of the major cell types in the BALF differed significantly between pretreatments. We found no association between post-exposure changes of BALF components and pulmonary function decrements. We conclude that IBU causes significant inhibition of O3-induced increases in respiratory tract PGE(2) and TxB(2) levels concomitant with a blunting of the spirometric response. This is consistent with the hypothesis that the products of AA metabolism mediate inhibition of inspiration. However, IBU did not alter the modest SRAW response to O3.

Adult↗

Mucociliary clearance of inhaled particles measured at 2 h after ozone exposure in humans.

Acute exposure of humans to ozone is known to acutely cause pulmonary function decrements, inflammation, and increased permeability of pulmonary epithelium. A single study in humans has also shown that mucociliary transport increases during acute ozone exposure. Because different responses have shown a different time course of recovery after exposure, it was important to examine mucociliary transport at a different time after the cessation of ozone exposure. We exposed 15 healthy male and female nonsmoking subjects, on different occasions, to clean air and 0.4 ppm ozone for 1 h while they exercised continuously. Pulmonary function was measured immediately before and after exposure and 90 min and 24 h after exposure. Between 2 and 5 h after each exposure, retention of inhaled 5-microns mass median aerodynamic diameter 99mTc-labeled Fe2O3 particles was measured. Each subject returned the next day for a final particle retention measurement. Despite significant changes in pulmonary function, there was no difference in mean whole lung retention time of particles between clean air [77.9 +/- 0.8 (SE) min] and ozone (78.0 +/- 0.8 min) exposures, indicating that mucociliary transport is unaffected by ozone exposure when it is measured 2 h after exposure.

Adolescent↗

Pulmonary function, airway responsiveness, and respiratory symptoms in asthmatics following exercise in NO2.

Two experiments were conducted to determine respiratory responses of persons with asthma performing intermittent moderate exercise while exposed to low concentrations of NO2. In the first, preliminary experiment, 13 male subjects, aged 19-35, with mild asthma were exposed on separate days in a chamber (natural breathing, 20 degrees C, 40% RH) to 0.30 ppm NO2 and to a control or "clean air" exposure (0.0 ppm NO2). Exposure included three 10-min periods of moderate treadmill exercise (VE = 44.5 liter/min), each followed by symptom measurement and pulmonary function testing. The average decrease in FEV1 following the initial 10 min exercise in 0.30 ppm was 11% which was significantly greater (p less than 0.05) than that observed in clean air (7%). Differences in FVC and SRaw were not significantly different at this time. Slight cough and dry mouth and throat were apparent only after the first exercise in NO2. After the second and third exercises, decreases in FEV1 and FVC and increases in SRaw were significantly greater in 0.30 than in 0.0 ppm NO2. Individual subject responses were variable. These results suggested that some asthmatics who perform moderate exercise while exposed to 0.30 ppm NO2 may experience bronchoconstriction and reduction in spirometric performance. Because of these preliminary findings, a more comprehensive, concentration-response experiment was conducted. Twenty-one male volunteers with mild asthma were exposed for 75 min with natural breathing to 0.0, 0.15, 0.30, and 0.60 ppm NO2. Exposure included three 10-min periods of moderate treadmill exercise (VE = 43 liter/min), each exercise followed by symptoms measurement and pulmonary function testing. In addition, airway responsiveness was measured two hr after each exposure by methacholine bronchial challenge testing. In the control exposures (0.0 ppm NO2), the exercise alone caused substantial decrements in pulmonary function. These decrements (as measured by decreases in FEV1 and FVC, and increases in SRaw) were not increased relative to the control exposure after any exercise session in any concentration of NO2. Furthermore, there was no overall group-averaged indication of a concentration-related effect of the NO2 on pulmonary function. Likewise, symptoms reported after NO2 exposure were not significantly different from those reported in clean air. Group-averaged airway responsiveness after exercise in NO2 was also not different from responsiveness after exercise in clean air. For only two subjects was there any indication of a concentration-related increase in airway responsiveness due to exposure to NO2.(ABSTRACT TRUNCATED AT 400 WORDS)

Adult↗

Airway sensitivity of asthmatics to sulfur dioxide.

The purpose of this study was to describe for asthmatic subjects the distribution of individual bronchial sensitivity to sulfur dioxide (SO2). Subjects were nonsmoking male asthmatics (n = 27) who were sensitive to inhaled methacholine. None of the subjects used corticosteroids or cromolyn sodium. Oral medications were withheld for 48 hr, inhaled medications for 12 hr prior to all testing. Each subject participated in four separate randomly ordered 10 min exposures to 0.00, 0.25, 0.50 and 1.00 ppm SO2 at 26 degrees C, 70% relative humidity. During exposures, subjects breathed naturally and performed moderate exercise (VE, normalized for body surface area = 21 1/m2 X min). Before and 3 min after exposure, specific airway resistance (SRaw) was measured by body plethysmography. Those subjects whose SRaw was not doubled by exposure to 1.00 ppm were also exposed to 2.00 ppm SO2. Dose response curves (relative change in SRaw, corrected for change in clean air vs SO2 concentration) were constructed for each subject. Bronchial sensitivity to SO2 [PC(SO2)], defined as the concentration of SO2 which provoked an increase in SRaw 100% greater than the response to clean air, was determined. Substantial variability in sensitivity was observed: for 23 subjects, PC(SO2) ranged between 0.28 and 1.90 ppm, while for the remaining 4 subjects, it was greater than 2.00 ppm SO2. The median PC(SO2) was 0.75 ppm SO2, and 6 subjects had a PC(SO2) of less than 0.50 ppm. PC(SO2) was not related (r = 0.31) to airway sensitivity to methacholine.

Adolescent↗