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Biomedical subjects

G E Hatch

Publications and source records attributed to G E Hatch.

At least 55 records · Page 3Linked to original sources

Pulmonary effects due to short-term exposure to oil fog.

Rats were exposed to an oil fog generated by flash vaporation and subsequent condensation of lightweight lubricating oil. Exposures were for 3.5 h/d, 4 d/wk, for 4 wk, at concentrations of 1.5, 0.5, or 0.0 mg/l and a particle size of approximately 1 micron. Samples of respiratory tissues were taken for histopathologic analyses, lavage fluid samples were collected, and pulmonary function measurements were made the day after the last exposure. An accumulation of macrophages within the alveolar lumen, an increase in lavage fluid protein content, and an increase in total cell content in lavage fluid due to an influx of polymorphonuclear leukocytes was noted in rats exposed at the 1.5-mg level. Also, for this exposure group there was an increase in lung wet and dry weight and an increase in end-expiratory volume, and pneumonitis was observed histopathologically in 4 of 10 male rats exposed. Pneumonitis was not observed among six female rats examined. Oil fog had no effect on total lung capacity, residual volume, vital capacity, lung compliance, or the distribution of ventilated air within the lung. Effects following exposure to 0.5 mg/l were limited to slight accumulation of macrophages in the alveolar lumen and an increase in the total cells in lavage fluid, which could not be attributed to an increase in any particular cell type.

Air Pollutants↗

Nitrogen dioxide exposure and lung antioxidants in ascorbic acid-deficient guinea pigs.

We have previously found that ascorbic acid (AA) deficiency in guinea pigs enhances the pulmonary toxicity of nitrogen dioxide (NO2). The present study showed that exposure to NO2 (4.8 ppm, 3 hr) significantly increased lung lavage fluid protein (a sensitive indicator of pulmonary edema) only in guinea pigs fed rabbit chow (a diet not supplemented with vitamin C) for at least 7 days, at which time lung AA was about 50% of normal. The rabbit chow diet did not cause reduced body weight as did commercial synthetic scorbutic diets, even when they were supplemented with AA. After 14 days of feeding rabbit chow, lung AA was reduced to 15% of control. At this time, alpha-tocopherol (AT) in the same lungs was reduced to 85% of control, and lung nonprotein sulfhydryls (NPSH) were increased to 114% of control. Exposure of the guinea pigs to NO2 (4.5 ppm, 16 hr) increased wet lung weight and further altered the antioxidants in deficient (but not normally fed) animals in the following manner: NPSH content was increased to 130% of control, AT was decreased to 74% of control, and AA was increased from 15 to 50% of control. These findings suggest that depletion of AA in guinea pigs removes an important defense against NO2. The lung appears to be able to partially compensate for the dietary lack of antioxidant by accumulating AA from other tissues and by increasing NPSH concentrations. However, sufficient exposure to NO2 leads to oxidation of AT and pulmonary edema. Conditions in which NO2 produced edema were accompanied by only a slight consumption of AT, and no detectable oxidation of lung AA or NPSH.

Animal Feed↗

Toxicity of particles emitted from combustion of waste crankcase oil: in vitro and in vivo studies.

The ever-rising cost of energy provides incentives for the utilization of low-cost waste crankcase oil (WCO) for space heating. Although WCO is known to contain toxic heavy metals, the potential health hazards of emissions and waste products resulting from the combustion of WCO are unknown. Thus, the toxicity of the emission particles and waste products from two different types of burners, a Dravo atomizing oil burner (AOB) and a Kroll vaporizing oil burner (VOB), is evaluated using automotive WCO. Samples are characterized by performing elemental analysis and scanning electron microscopy. Both burners emitted fine (less than or equal to 3 microns), respirable particles. The AOB emission particles contained high concentrations of toxic heavy metals, especially Pb, which showed concentrations as high as 7.5%. The VOB retained a significant amount of heavy metals in the burner residue and emitted a much smaller quantity into the air. The toxicity of AOB emission particles, VOB emission particles, and VOB waste residue is evaluated in three bioassay systems, including a rabbit alveolar macrophage (RAM) cytotoxicity in vitro assay, an intratracheal injection infectivity assay, and a peritoneal irritancy test in mice. The emission particles from both burners and leachate from VOB residue produce a dose-related reduction in viability and cellular adenosine triphosphate (ATP) in alveolar macrophages following 20-hr exposure. Acidity of the RAM medium due to the presence of VOB emission particles and waste leachate contributes to its toxicity.(ABSTRACT TRUNCATED AT 250 WORDS)

Air Pollutants↗

Species comparison of acute inhalation toxicity of ozone and phosgene.

A comparison of the concentration-response effects of inhaled ozone (O3) and phosgene (COCl2) in different species of laboratory animals was made in order to better understand the influence of the choice of species in inhalation toxicity studies. The effect of 4-h exposures to ozone at concentrations of 0.2, 0.5, 1.0, and 2.0 ppm, and to COCl2 and 0.1, 0.2, 0.5, and 1.0 ppm was determined in rabbits, guinea pigs, rats, hamsters, and mice. Lavage fluid protein (LFP) accumulation 18-20 h after exposure was used as the indicator of O3- and COCl2-induced pulmonary edema. All species had similar basal levels of LFP (250-350 mg/ml) when a volume of saline that approximated the total lung capacity was used to lavage the collapsed lungs. Ozone effects were most marked in guinea pigs, which showed significant effects at 0.2 ppm and above. Mice, hamsters, and rats showed effects at 1.0 ppm O3 and above, while rabbits responded only at 2.0 ppm O3. Phosgene similarly affected mice, hamsters, and rats at 0.2 ppm and above, while guinea pigs and rabbits were affected at 0.5 ppm and above. Percent recovery of lavage fluid varied significantly between species, guinea pigs having lower recovery than other species with both gases. Lavage fluid recovery was lower following exposure to higher levels of O3 but not COCl2. Results of this study indicate that significant species differences are seen in the response to low levels of O3 and COCl2. These differences do not appear to be related in a simple manner to body weight.

Animals↗

Pulmonary biochemical effects of inhaled phosgene in rats.

Three exposure regimens were used to study the time course of indicators of lung damage and recovery response to single or repeated exposures to phosgene (COCl2). Rats were sacrificed immediately or throughout a 38-d recovery period after inhalation of 1 ppm COCl2 for 4 h, at intervals during a 7-h exposure to 1 ppm phosgene, or at several time points throughout a 17-d exposure to 0.125 and 0.25 ppm COCl2 (4 h/d, 5 d/wk) and during a 21-d recovery period. Regimen 1 revealed significantly elevated lung wet weight, lung nonprotein sulfhydryl (NPSH) content, and glucose-6-phosphate dehydrogenase (G6PD) activity that stayed elevated for up to 14 d. A significant decrease in body weight and food intake was observed 1 d after exposure. Regimen 2 caused a slight depression in NPSH content but did not affect G6PD activity. Regimen 3 animals showed sustained elevations in lung wet weight, NPSH content, and G6PD activity after 7 d of exposure. No significant changes in these endpoints were observed for the 0.125 ppm COCl2 group. No consistent elevation in hydroxyproline content was seen at either exposure concentration. Light microscopic examination of lung tissue exposed to 0.25 ppm COCl2 for 17 d revealed moderate multifocal accumulation of mononuclear cells in the centriacinar region. In summary, exposure to COCl2 caused changes similar in most ways to those observed for other lower-respiratory-tract irritants.

Animals↗

Inhalable particles and pulmonary host defense: in vivo and in vitro effects of ambient air and combustion particles.

The ability of particulate air pollutants (and possible constituents) to alter pulmonary host defenses was examined using an in vitro alveolar macrophage cytotoxicity assay and an in vivo bacterial infectivity screening test which employed intratracheal injection of the particles. A wide range of response between particles was seen at the 1.0-mg/ml level in vitro and the 0.1-mg/mouse level in vivo. A sample of fluidized-bed coal fly ash, bentonite, asbestos, some ambient air particles, and heavy metal oxides greatly increased susceptibility to pulmonary bacterial infection. Most coal fly ash samples and some air particles caused moderate increases in infectivity, while diesel particulates, volcanic ash, and crystalline silica caused only small increases. Cytotoxic effects on macrophages in vitro were observed with most of the particles. The in vivo and in vitro assays produced a similar ranking of toxicity; however, not all particles that were highly cytotoxic were potent in increasing bacterial infectivity. Increased toxicity measurable by either assay often appeared to be associated with small size or with the presence of metal in the particles.

Air Pollutants↗

Inhalation studies of Mt. St. Helens volcanic ash in animals. II. Lung function, biochemistry, and histology.

Rats were exposed by inhalation to 9.4 mg/m3 size-fractionated volcanic ash for 5 days (2 hr/day) and examined for changes in pulmonary function and histology for periods of up to 1 year. Fine-mode volcanic ash, SO2, and a combination of ash and SO2 produced no observable effects in normal rats and rats with elastase-induced emphysema. However, there was a mild irritant response to SO2 which was not influenced by the volcanic ash. Rats injected intratracheally with fine-mode volcanic ash or saline showed no evidence of pulmonary alterations after 6 months. Those injected with coarse-mode volcanic ash showed minor pulmonary functional changes, histologically detectable alveolitis, and small increases in lung weight. In contrast, quartz-injected rats showed large alterations in pulmonary function, lung weight, hydroxyproline levels, and large areas of lung consolidation and fibrosis.

Animals↗

Inhalation studies of Mt. St. Helens volcanic ash in animals. III. Host defense mechanisms.

The effects of inhalation exposure of mice or rats to 9.4 mg/m3 volcanic ash, 2.5 mg/m3 SO2, or both on host defense mechanisms were assessed. Cytologic changes in pulmonary lavage fluid included an increase in percentage polymorphonuclear leukocytes due to SO2 exposure and an increase in eosinophils due to ash. SO2 and ash also produced decreases in percentage alveolar macrophages. In the case of ash-exposed animals, this decrease was offset by an increase in lymphocytes. Total cell counts and viability were not affected by any of the exposures. Pulmonary clearance mechanisms were affected in that there were both decreased alveolar macrophage phagocytic capability following ash and ash + SO2 exposures and depressed ciliary beat frequency attributable to ash exposure. None of the inhalation exposures caused increases in susceptibility to an immediate or 24 hr postexposure aerosol challenge with Streptococcus. However, intratracheal instillation of both fine- and coarse-mode volcanic ash caused slight but significant increases in mortality due to bacterial challenge 24 hr after the instillation. The phytohemagglutinin-induced blastogenic response of splenic lymphocytes from exposed animals did not differ significantly from that of control lymphocytes, although the lipopolysaccharide-induced blastogenic response was enhanced. Ash exposure had no effect on susceptibility to murine cytomegalovirus. In summary, volcanic ash alone or in combination with SO2 had only minimal effects on certain host defense mechanisms.

Air Pollutants↗

Comparison of lung antioxidant levels in humans and laboratory animals.

Basal lung concentrations of ascorbic acid (AA), nonprotein sulfhydryls (NPSH), and alpha-tocopherol (alpha-T) were determined in rabbits, guinea pigs, rats, hamsters, mice, domestic pigs and sheep, and in human lung samples obtained from cancer surgery patients. Significant differences were found among the laboratory animals: AA levels ranged from 25.6 mg% (mg/100 g wet weight) in hamsters to 41.7 mg% in mice, NPSH from 50.9 mg% in rats to 84.7 mg% in rabbits, and alpha-T from 1.01 mg% in hamsters to 2.74 mg% in rats. Porcine lung AA and NPSH concentrations approximated those of the laboratory animals and their alpha-T levels were the highest of all species studied. Sheep lung AA levels were comparable to those in the other species, although their NPSH and alpha-T levels appeared to be lower. Human lung concentrations of NPSH (5.2 mg%) and alpha-T (0.85 mg%) appeared low, whereas the mean AA concentration (22.1 mg%) was similar to that of laboratory animals. A partial correlation was found between AA and alpha-T levels and between NPSH and alpha-T levels in the 5 laboratory animal species.

Adult↗

Effect of silica and volcanic ash on the content of lung alveolar and tissue phospholipids.

Silica or volcanic ash (VA) was administered to rats via intratracheal instillation and the changes in extracellular (i.e., lavage fluid) and tissue phospholipids, as well as various biochemical parameters, were monitored over a 6-month period. VA produced relatively minor (up to 2.8-fold) increases in lung tissue or lavage fluid phospholipids that were maximal at 1 month postinstillation. These increases were quantitatively similar to the increases in protein and DNA content of lung tissue and lavage fluid induced by VA and, thus, may be attributable to hypercellularity and accumulation of cellular breakdown products in the alveolar lumen. Instillation of silica produced a much greater (up to 11-fold) increase than VA in total phospholipid over time, primarily due to a 14-fold increase in phosphatidylcholine (PC). The accumulation of PC was more pronounced in the lavage fluid during the first month following silica instillation, but thereafter progressed more rapidly in the lung tissue. The relatively small increases (1.3- to 3.5-fold) in other phospholipids induced by silica appeared to be nonspecific, since they did not differ greatly from the increases in lung weight, DNA, and protein. Collectively, these results indicate that intratracheal instillation of silica induces selective accumulation of lung PC, implying enhanced synthesis and secretion of pulmonary surfactant from alveolar epithelial Type II cells into the lumen.

Air Pollutants↗

Functional and biochemical indicators of pneumoconiosis in mice: comparison with rats.

Mice were injected intratracheally with silica or Mt. St. Helens volcanic ash (0.2 mg/g body weight) and examined 6 mo later for changes in pulmonary function, histology, and hydroxyproline content. Results were compared with a similar study using rats. Mice injected with volcanic ash showed significant changes only in wet lung weights. Those injected with silica showed an approximate doubling of lung wet weight and dry weight and hydroxyproline content. Larger increases in lung weight were seen if lymph nodes were left attached. Lung compliance, total lung capacity, and the shape of the pressure-volume curve of the lung were changed as much as 22% in the silica-treated mice. A mild degree of fibrosis with no dense lung consolidation was noted microscopically in silica-treated mice. In contrast, silica-treated rats showed dense lung consolidation, threefold to fivefold increases in both wet and dry lung weights and hydroxyproline content, and up to 40% reductions in pulmonary function measurements. It is concluded that Swiss albino mice develop a milder degree of fibrosis than similarly treated Sprague-Dawley rats and that both biochemical and functional indicators are effective in detecting pneumoconiosis in these species.

Animals↗

Correlation of effects of inhaled versus intratracheally injected males on susceptibility to respiratory infection in mice.

Effects of intratracheally administered air pollutant chemicals on susceptibility of mice to infection by aerosolized bacteria were compared with effects of the same chemical previously studied by the inhalation route. Out of 22 compounds previously studied by inhalation, the same 3 (CdSO4, CuSO4, and ZnSO4) that caused significantly increased mortality because of infection after a 3-h exposure to 1 to 2 mg/m3 showed large (greater than or equal to 40% over sham injected) mortality increases when administered by intratracheal injection at lung concentrations calculated to be equivalent to those achieved during inhalation exposures (0.6 to 1.2 microgram). Dose-effect curves of these compounds were similar by the 2 routes. Five of the compounds caused a moderate (20 to 30%) enhancement in the mean excess mortality at concentrations of 2 to 3 microgram/animal. The remaining compounds, which showed no significant effect by inhalation, also showed no effect when given by intratracheal injection. Thus, similar effects on susceptibility to lung bacterial infection were seen whether chemicals were deposited in te lung by inhalation or by intratracheal injection.

Aerosols↗

Chemiluminescence of phagocytic cells caused by N-formylmethionyl peptides.

N-formylmethionyl (F-Met) peptides, when added alone to macrophages or polymorphonuclear leukocytes (PMN), were found to induce a chemiluminescent response of shorter duration than that produced by the commonly employed particulate stimulant, zymosan. The cellular nature of F-Met peptide-induced chemiluminescence was indicated by its dependence on cell concentration, and by its inhibition by cell disruption, heat inactivation, or previous maximal stimulation by the peptides. Comparison of PMN and macrophages from different species showed that the maximal chemiluminescent response seen in the dose-response curve of F-Met- Phe was different in different cell types. Chemiluminescence reached highest values in human PMN, it was intermediate in guinea pig macrophages and PMN, and in rabbit PMN; but it was nonexistent in rabbit alveolar macrophages and very low in rabbit peritoneal macrophages. A definite relationship was observed between peptide structure and chemiluminescent activity. Met-Phe, F- Met and Phe were inactive even at millimolar concentrations, while F-Met-Phe caused chemiluminescence at micromolar concentrations. Four active peptides were tested in guinea pig, rabbit, and human PMN, and in guinea pig alveolar and peritoneal macrophages. The relative activity of these peptides was the same in all cells studied, e.g. F-Met-Leu-Phe >> F-Met-Phe > F-Met-Val > F- Met-Ala. The values of ED50 for each peptide were also comparable to previously reported ED50 values of these peptides in inducing lysosomal enzyme release. These results were seen both in the presence and absence ofthe chemiluminescent oxidant indicator, luminol. Low concentrations of superoxide dismutase (10 mug/ml) completely inhibited chemiluminescence caused by the F-Met peptides, suggesting the involvement of 0(2)(-) or O(2)(-)-derived compounds in this response. Sodium azide, an inhibitor of peroxidase reactions, had either no effect or a slight inhibitory effect on chemiluminescence. However, when the extracellular release of lysosomal enzymes was induced by cytochalasin B, an azide- inhibitable enhancement of chemiluminescence was seen in PMN, but not in macrophages. This effect appears to be correlated with the presence of granule-associated myeloperoxidase. Although azide-inhibitable peroxidases could be a potential source of light, they did not appear to be a significant contributor in these experiments. Based on these results and on those of previous investigators, we postulate that the F-Met-peptides stimulate 0(2)(-) production in addition to stimulating lysosomal enzyme release and chemotaxis. The similar structure- activity relationship which appears to exist for these processes may indicate that they are all initiated by a single receptor mechanism. Since F-Met peptides are formed in bacteria it is likely that their actions represent an important physiologic response.

Animals↗

A simplified procedure for cyclic nucleotide radioimmunoassay and its application to human blood leukocytes.

Rapid treatment of leukocyte suspensions was found to be an effective alternative to acid treatment in the preparation of these cells for radioimmunoassay of cyclic GMP and cyclic AMP. A 2-sec heating to boiling temperature, followed by sonication and micropore filtration, was employed. This procedure adequately inactivated or removed enzymes and binding proteins that can alter cyclic nucleotide concentrations or otherwise interfere with the radioimmunoassay. Moreover, heating in this manner did not appear to affect the stability of cyclic nucleotides or cause significant formation of cyclic GMP from endogenous GTP. Recovery of cyclic nucleotides after heating and filtration was high (89-96%), making possible the measurement of both cyclic GMP and cyclic AMP in small cellular samples. Variation in cyclic nucleotide recovery was small (+/- 2-4% SD), therefore individual recovery determinations were unnecessary.

Blood Proteins↗