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Biomedical subjects

A F Gunnison

Publications and source records attributed to A F Gunnison.

16 recordsLinked to original sources
PubMed1992

Enhanced inflammatory response to acute ozone exposure in rats during pregnancy and lactation.

Experimental evidence from several studies suggests that pregnant animals and women are more susceptible to oxidants than nonpregnant controls. In the study reported here, we sought to determine whether pregnant rats are more sensitive than age-matched virgin females to the inflammatory effects of ozone, a gaseous oxidant of considerable environmental significance. Rats at several stages of pregnancy and lactation, as well as age-matched virgin females, were exposed to 1 ppm ozone for 6 hr. Controls were sham-exposed to pure air for an identical period of time. Bronchoalveolar lavage was performed 24 hr after the beginning of exposure, and components of the lavage fluid considered to be indicators of inflammation were used to assess the severity of pulmonary inflammation. The results of this experiment showed that significantly enhanced sensitivity to ozone-induced pulmonary inflammation develops during pregnancy, is maintained during lactation, and disappears following lactation. Implicit in this pattern of differential sensitivity in rats is the possibility of a similar pattern of inflammatory response in analogous groups of humans as well as the potential for applicability to other oxidative pollutants.

Animals↗
PubMed1992

Age-dependence of responses to acute ozone exposure in rats.

Previous work from this laboratory demonstrated that neonatal rats and postweanling rabbits are more sensitive to ozone-induced stimulation of pulmonary arachidonic acid (AA) metabolism than are young adults (Fundam. Appl. Toxicol. 15, 779.) In the study reported here, we have extended our initial investigation to include the influence of animal age on temporal aspects of pulmonary AA metabolism and several other responses to brief exposures to 1 ppm ozone. Rats of discrete ages ranging from 13 days to 16 weeks were exposed to 1 ppm ozone or to air for 2, 4, or 6 hr. Immediately following exposure the lungs were lavaged with six consecutive volumes of phosphate-buffered saline and the acellular fluid from the first lavage volume recovered was analyzed for its content of prostaglandin E2 (PGE2), protein, and lactate dehydrogenase. Leukocytes recovered by lavage were quantitated and characterized by viability and percentage of polymorphonuclear (PMN) cells. Several lines of evidence verified that PGE2 was produced by the lung as a consequence of ozone exposure and that its concentration in the fluid from the first lavage was a reasonably good index of pulmonary AA metabolism to prostanoids. We also demonstrated that the lavage process itself stimulates the lung, resulting in increased AA metabolism to prostanoids that were recovered in the second and following lavage volumes. The time course of PGE2 production by the ozone-exposed lung varied considerably with animal age. Neonatal rats 13 days of age were the most sensitive to ozone stimulation. At 2 hr of exposure, PGE2 concentration in the first lung lavage of these animals peaked at values approximately two orders of magnitude above controls and then decreased sharply with continued exposure. Adults and older neonates (18 days of age) were much less responsive to 2-hr exposures; however, continued exposure of these rats for up to 6 hr resulted in increasing PGE2 concentration in the first lung lavage. Other responses showed various degree of age dependence. The percentage of lavaged leukocytes that were nonviable (i.e., trypan blue-positive) showed a strong inverse correlation with animal age. In 13-day-old rats that were exposed for 6 hr, the percentage of dead leukocytes reached nearly 50%. In addition, sheets or clumps of dead cells that were judged to be epithelial cells were lavaged from these animals. Conversely, 16-week-old adult males exposed to ozone for 6 hr showed little evidence of damage to cells of the respiratory tract.(ABSTRACT TRUNCATED AT 400 WORDS)

Age Factors↗
PubMed1990

Modulation of pulmonary eicosanoid metabolism following exposure to sulfuric acid.

Eicosanoids (arachidonic acid metabolites) are potent biological mediators. Modulation of their metabolism by air pollutants may be a possible factor in the pathogenesis of environmentally related lung disease. Sulfuric acid (H2SO4) aerosols are components of ambient air in many areas. Rabbits were exposed to H2SO4 (0.3 microns) at 250, 500, or 1000 micrograms/m3 for 1 hr/day for 5 days. They were then euthanized, the lungs lavaged, and eicosanoid analyses performed by radioimmunoassay of acellular lavage fluid. An exposure-concentration-dependent decrease in levels of prostaglandins E2 and F2 alpha and thromboxane B2 was found; no change in leukotriene B4 was observed. Tracheal explants exposed to acidic environments in vitro also showed reduced production of PGE2, PGF2 alpha, and TxB2. Incubation with sodium sulfate (Na2SO4) showed no effect of the sulfate ion (SO4(2-)). This study, the first to examine eicosanoid production after in vivo exposure to pure H2SO4 droplets, indicates that such exposure can modulate arachidonic acid metabolism, and that this is likely due to the deposition of hydrogen ion (H+) on target tissue.

Aerosols↗
PubMed1990

Age-dependent effect of ozone on pulmonary eicosanoid metabolism in rabbits and rats.

Acute exposures to ozone have previously been shown to cause quantitative changes in the spectrum of arachidonic acid (AA) metabolites in lung lavage fluid. Since age appears to be an important variable in the toxicity of inhaled ozone, we investigated its effect on ozone-induced changes in pulmonary eicosanoid metabolism. Rats and rabbits ranging in age from neonates to young adults were exposed either to air or to 1 ppm ozone for 2 hr. Lung lavage fluid was collected within 1 hr following exposure and analyzed for its content of selected eicosanoids. In both species, there was a pronounced effect of age on ozone-induced pulmonary eicosanoid metabolism. Ozone-exposed animals at the youngest ages examined had severalfold greater amounts of two products of the cyclooxygenase pathway, prostaglandin E2 (PGE2) and prostaglandin F2 alpha (PGF2 alpha), than did age-matched controls. This effect lessened and eventually disappeared as the animals grew toward adulthood. In rabbits, ozone also induced increases in 6-keto-prostaglandin F1 alpha and thromboxane B2, but these changes were of lesser magnitude and evident only in the youngest rabbits exposed. There was no observed effect of ozone on lung lavage content of leukothriene B4. Indices of nonspecific pulmonary damage, i.e., protein concentration in lung lavage fluid and total number and viability of lavaged lung cells, were affected by ozone exposure, but not in an age-dependent manner that correlated with changes in pulmonary eicosanoid metabolism. In vitro ozone exposure of lung macrophages from naive rabbits of the same age range as those exposed in vivo demonstrated that ozone is capable of stimulating the elaboration of PGF2 alpha and especially PGE2. However, the increase in lavage fluid PGE2 and PGF2 alpha caused by ozone inhalation could not be attributed to macrophage metabolism conclusively since elaboration of PGE2 and PGF2 alpha by cultured macrophages was not enhanced by prior in vivo ozone exposure. In an ancillary study it was shown that 15-hydroxyprostaglandin dehydrogenase (PGDH) activity in rabbit lung homogenates was not affected by prior exposure to ozone, indicating that the increase in lung lavage fluid eicosanoids that occurred in these animals could not be explained by inhibition of PGDH.

Aging↗
PubMed1990

Pulmonary arachidonic acid metabolism following acute exposures to ozone and nitrogen dioxide.

Ozone (O3) and nitrogen dioxide (NO2) are common air pollutants, and exposure to these gases has been shown to affect pulmonary physiology, biochemistry, and structure. This study examined their ability to modulate arachidonic acid metabolites (eicosanoids) in the lungs. Rabbits were exposed for 2 h to O3 at 0.1, 0.3, or 1 ppm; NO2 at 1, 3, or 10 ppm; or to a mixture of 0.3 ppm O3 and 3 ppm NO2. Groups of animals sacrificed either immediately or 24 h after each exposure underwent broncho-pulmonary lavage. Selected eicosanoids were assessed in lavage fluid by radioimmunoassay. Increases in prostaglandins E2 (PGE2) and F2 alpha (PGF2 alpha) were found immediately after exposure to 1 ppm O3. Exposure to 10 ppm NO2 resulted in a depression of 6-keto-PGF1 alpha, while thromboxane B2 (TxB2) was elevated after exposure to 1 ppm NO2 and depressed following 3 and 10 ppm. The O3/NO2 mixture resulted in synergistic increases in PGE2 and PGF2 alpha, with the response appearing to be driven by O3. This study has demonstrated that acute exposure to either O3 or NO2 can alter pulmonary arachidonic acid metabolism and that the responses to these oxidants differ, both quantitatively and qualitatively.

Air Pollutants↗
PubMed1988

The effect of inhaled sulfur dioxide and systemic sulfite on the induction of lung carcinoma in rats by benzo[a]pyrene.

In a previous study at this Institute, inhaled sulfur dioxide (SO2) was shown to enhance the induction by inhaled benzo[a]pyrene (BaP) of squamous cell carcinoma (SQCA) of the respiratory tract of rats (S. Laskin, M. Kuschner, A. Sellakumar, and G. V. Katz, 1976, In "Air Pollution and the Lung," pp. 190-213). We attempted to confirm and extend this finding by using an experimental protocol intended to illuminate the role of SO2. Rats were treated with BaP by 15 consecutive weekly intratracheal instillations. Some of these rats were simultaneously exposed either to SO2 by inhalation or to sulfite/bisulfite anions that accumulated systemically from endogenous generation in rats with induced sulfite oxidase deficiency. The total treatment period spanned 21 weeks, after which the rats were observed for the development of tumors. BaP-treated rats began to die with SQCA of the respiratory tract at approximately 200 days after the first BaP treatment and at 2 years after the first treatment nearly all rats in the BaP-treated groups had died, most with SQCA. Survival in the control groups was excellent and the health of all groups (aside from pulmonary SQCA in BaP-treated groups) was also excellent. The probability of dying with a pulmonary SQCA in the experimental groups treated with BaP, BaP plus inhaled SO2, and BaP plus systemic sulfite/bisulfite was calculated by the logrank analysis. The data sets of SQCA probability from these groups were not statistically different (i.e., P greater than 0.05) by the chi 2 test indicating that, in this experiment, neither inhalation exposure to SO2 nor systemic exposure to sulfite/bisulfite anions affected the induction of SQCA of the lung by intratracheally instilled BaP. We conclude that the results of this study do not support an etiological role for either SO2 or sulfite/bisulfite anions in the induction of SQCA of the respiratory tract by BaP.

Administration, Inhalation↗
PubMed1987

Distribution, metabolism and toxicity of inhaled sulfur dioxide and endogenously generated sulfite in the respiratory tract of normal and sulfite oxidase-deficient rats.

We report on the distribution, metabolism, and toxicity of sulfite in the respiratory tract and other tissues of rats exposed to endogenously generated sulfite or to inhaled sulfur dioxide (SO2). Graded sulfite oxidase deficiency was induced in several groups of rats by manipulating their tungsten to molybdenum intake ratio. Endogenously generated sulfite and S-sulfonate compounds (a class of sulfite metabolite) accumulated in the respiratory tract tissues and in the plasma of these rats in inverse proportion to hepatic sulfite oxidase activity. In contrast to this systemic mode of exposure, sulfite exposure of normal, sulfite oxidase-competent rats via inhaled SO2 (10 and 30 ppm) was restricted to the airways. Minor pathological changes consisting of epithelial hyperplasia, mucoid degeneration, and desquamation of epithelium were observed only in the tracheas and bronchi of the rats inhaling SO2, even though the concentration of sulfite plus S-sulfonates in the tracheas and bronchi of these rats was considerably lower than that in the endogenously exposed rats. We attribute this histological damage to hydrogen ions stemming from inhaled SO2, not to the sulfite/bisulfite ions that are also a product of inhaled SO2. In addition to the lungs and trachea, all other tissues examined, except the testes, appeared to be refractory to high concentrations of endogenously generated sulfite. The testes of grossly sulfite oxidase-deficient rats were severely atrophied and devoid of spermatogenic cells.

Administration, Inhalation↗
PubMed1987

Sulfite hypersensitivity. A critical review.

Sulfiting agents (sulfur dioxide and the sodium and potassium salts of bisulfite, sulfite, and metabisulfite) are widely used as preservatives in foods, beverages, and pharmaceuticals. Within the past 5 years, there have been numerous reports of adverse reactions to sulfiting agents. This review presents a comprehensive compilation and discussion of reports describing reactions to ingested, inhaled, and parenterally administered sulfite. Sulfite hypersensitivity is usually, but not exclusively, found within the chronic asthmatic population. Although there is some disagreement on its prevalence, a number of studies have indicated that 5 to 10% of all chronic asthmatics are sulfite hypersensitive. This review also describes respiratory sulfur dioxide sensitivity which essentially all asthmatics experience. Possible mechanisms of sulfite hypersensitivity and sulfur dioxide sensitivity are discussed in detail. Sulfite metabolism and the role of sulfite oxidase in the detoxification of exogenous sulfite are reviewed in relationship to the etiology of sulfite hypersensitivity.

Administration, Oral↗
PubMed1979

Preferential S-sulfonate formation in lung and aorta.

S-sulfonate (S-SO-3) compounds have previously been identified as metabolites of sulfite in the plasma of several species of mammals [6--8]. We now report the formation of non-diffusible and relatively stable S-sulfonates in the aorta and lung lobes of rabbits exposed intravenously to constant arterial sulfite concentrations of approx. 550 microM. Under these conditions the kinetics of S-SO-3 formation were first order with coefficients in the range of 0.3--0.4 h-1 and asymptotic concentrations of approx. 900 and 9000 nmol S-SO-3/g dry wt. of lung and aorta respectively. The kinetics of this reaction in aorta tissue were closely approximated in vitro. Clearance of S-SO-3 from both lungs and aorta appeared to be first order with a half-life of 2--3 days.

Animals↗
PubMed1978

Species variability in plasma S-sulfonate levels during and following sulfite administration.

It has been shown that S-sulfonate compounds (R-S-SO-3) are produced by the action of sulfite on reactive disulfide bonds [4,5]. Plasma S-sulfonate production was determined as a function of sulfite ingestion and intraperitoneal injection in rats, mice and rhesus monkeys. The tendency of these species and of the rabbit [8] to produce S-sulfonates in plasma was related to the availability of sulfite and of reactive disulfide bonds and to the stability of plasma protein S-sulfonates. The rhesus monkey and the rabbit accumulated plasma S-sulfonates much more readily than did the rat, while the mouse produced little, if any, under the same test conditions. Plasma protein S-sulfonate fractions in the rat and rhesus monkey were characterized by half-lives of approximately 4 and 8 days respectively. The sensitivity and precision of the analytical method for plasma protein S-sulfonate were improved by incorporation of 35S into the outer sulfur atom of the S-sulfonate moiety (R-S-35SO-3).

Animals↗
PubMed1976

Personal sampler for nitrogen dioxide.

A new type of personal sampler for gases in air, originally reported from this laboratory, has been adapted to measurement of NO2. The sampler depends on the transfer of NO2 by diffusion to a triethanolamine coated collector at the sealed end of a tube; the open end of the tube is exposed to the test environment. The devices are accurate, light, simple to use and have very good shelf life before and after sampling.

Air Pollutants↗