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Type 2 pneumocytes are progenitor cells of alveolor epithelium and important for reepithelialization following lung injury. This study examined the role of persistent versus transient mitogen-activated protein (MAP) kinase (extracellular signal-regulated kinase; ERK) in type 2 cell proliferation. Three different types of agents; epidermal growth factor (EGF), 12-O-tetradecanoylphorbol-13-acetate (TPA), and fetal bovine serum (FBS) induced different patterns of ERK activation. FBS induced a strong and persistent MAP kinase response, whereas the effect of EGF was transient with a strong activation at 5 minutes and only a slight stimulation at 4 hours. The TPA response was more prolonged than the EGF response, but not by far as strong and persistent as the FBS response. Activation by EGF and TPA and the early response induced by FBS were strongly reduced by the MEK inhibitor PD98059. The sustained FBS-induced ERK activation was inhibited by approximately 50%. The total number of cell, the percentage of cells in S and G2/M phase of the cell cycle and the incorporation of 3H-thymidine into DNA were strongly increased in response to FBS, whereas EGF and TPA were without effect. The proliferation was reduced by approximately 50% after pretreatment with PD98059. The results indicate that a persistent ERK activation of a critical size leads to type 2 cell proliferation, and that the proliferative response may also depend on a MEK-independent ERK activation.

CCAAT/enhancer-binding proteins (C/EBP) constitute a family of transcription factors that are involved in regulation of proliferation and differentiation in several cell types. In epithelial lung cells the C/EBP alpha isoform seems to play a role in the regulation of surfactant proteins (SP) and Clara cell specific protein (CCSP), whereas the roles of C/EBP beta and C/EBP delta are unclear. We have examined the protein levels of C/EBP delta in bronchiolar Clara cells and alveolar type 2 cells, and its relation to the expression of lung specific proteins and cell proliferation. The protein expression of C/EBP delta was high in freshly isolated Clara cells compared to type 2 cells. In both cell types C/EBP delta levels increased during culture. Alterations of the levels of C/EBP delta did not correspond with the proliferation levels of Clara cells, but seemed to correspond in type 2 cells. Clara cell secretory protein (CCSP) was highly expressed in freshly isolated Clara cells, in contrast to type 2 cells. SP-D and CYP2B1 were expressed at somewhat higher levels in Clara cells than in type 2 cells, whereas SP-A exhibited highest expression in type 2 cells. During culture the levels of all these lung proteins were strongly reduced. However, compared to with serum we found an increase in CCSP in Clara cell cultures without serum, and this correlated with an increase in C/EBP delta. Overall our in vitro data suggest that C/EBP delta alone is not related to the maintenance of proteins involved in differentiation.

The Clara-cell secretory protein (CCSP) is a cell-specific differentiation marker for the bronchiolar Clara cell. Isolated rat Clara and alveolar type 2 cells kept in primary culture proliferate and dedifferentiate, providing the opportunity to study differentiation-dependent mechanisms. In freshly isolated Clara cells, high levels of CCSP and the corresponding mRNA were detected. During culture in vitro, these levels decreased. In the type 2 cell fraction, low levels of CCSP were detected, which decreased further during culture. A promoter fragment of the rat CCSP gene encompassing the sequence from -188 to +53 was able to drive high-level expression of reporter genes in transfected Clara cells. Reporter gene expression in transfected type 2 cells was markedly lower, and no expression could be detected in alveolar macrophages. Expression of transcription factors previously described to stimulate CCSP expression appeared not to parallel CCSP levels in the primary Clara cells. However, expression of the transcription factor C/EBP alpha correlated with the CCSP expression pattern. In electrophoretic mobility shift assays, we were able to demonstrate binding of C/EBP alpha from rat Clara cell nuclear extracts to an element located 85 bp upstream of the start site of transcription. Overexpression of C/EBP alpha increased expression from the CCSP -188 promoter fragment up to fivefold in NCI-H441-cells and 30-fold in A549-cells, establishing the functional importance of C/EBP alpha. Our results show that primary cultures of Clara cells constitute a useful model for investigating terminal airway differentiation and suggest a role for C/EBP-factor(s) in this process.

Ozone in the ambient air may induce adverse health effects. It is a potent oxidant which can damage all parts of the respiratory tract. Ozone exposure leads to health effects as diverse as reduced pulmonary function, increased airway reactivity, lung inflammation, increased respiratory symptoms/illness and higher mortality. Several of these acute effects have been observed in experiments involving controlled exposure at concentrations as low as 160 micrograms/m3, and in epidemiologic studies with ozone concentrations of 100 micrograms/m3 or higher. As yet, it is unclear whether repeated exposure to ozone causes irreversible pulmonary changes in humans, but such effects have been indicated in studies in animals. Marked interindividual variation in sensitivity and responsiveness to ozone has been demonstrated. To protect the population the Norwegian Pollution Control Authority recommends 100 micrograms/m3 and 80 micrograms/m3 as maximum ozone air quality guidelines for 1-hr and 8-hr averages, respectively. As a consequence of the EEA agreement, Norway is required to announce to the public when 1-hr average ozone concentrations exceed 180 micrograms/m3.

Bronchiolar Clara cells and alveolar type 2 cells of the lung are known to express relatively high levels of P450 enzymes compared to other pulmonary cells. Populations of enriched type 2 cells and Clara cells were isolated from rat lung by a procedure including lung perfusion, protease digestion, centrifugal elutriation, and differential attachment. Alveolar macrophages were removed by lavage. The purity of the type 2 cell-enriched population was approximately 90%, and the purity of the Clara cell-enriched population was 40-50%. Both type 2 cells and the cells of the Clara cell-enriched population proliferated in culture. CYP2B1 mRNA was expressed approximately to the same level in type 2 cells and the Clara cell-enriched population. The mRNA levels remained roughly constant for both cell types throughout the culture period, except for an early transient reduction. The apoenzyme level of CYP2B1 was 2-3 times higher in freshly isolated cells of the Clara cell-enriched population than in the type 2 cells. Both epithelial cell types showed decreased level of CYP2B1 apoenzyme in culture. The differences in the CYP2B1 mRNA and apoenzyme expression levels in freshly isolated cells and cultured cells suggest the existence of a post-transcriptional regulatory mechanism for CYP2B1 expression in lung cells. The characterization of specific functions of lung cells in culture, such as P450 gene expression, provides necessary information for the use of the cells in in vitro pulmonary toxicology.

Isolated lung cells constitute a valuable system for studying mechanisms involved in chemically induced toxicity in the lung. Different lung cells isolated from various species may be studied. Bronchiolar Clara and alveolar type 2 cells produce important lung-specific proteins, hold a major role in the metabolism of xenobiotics and serve as progenitor cells for other lung cell types. They are possible target cells in lung carcinogenesis. Alveolar macrophages play an important role in lung defence and in inflammatory responses. In the present study we have characterised chemically induced DNA damage, apoptosis, changes in cell cycle progression, transformation and alterations in gene expression in these specific lung cells isolated from rat, rabbit and human. Major differences between the cell types and the various species in the induction of DNA damage by chemicals were found, as measured by the 32P-postlabelling and alkaline filter elution techniques. Benzo(a)pyrene and hydrogen fluoride were found to induce apoptosis in the isolated cells as measured by microscopical analysis and flow cytometry. The function of various important tissue- or cell type specific proteins (CYP 2B1, Clara cell protein) and/or cellular signal transduction pathways constitute important targets that may be affected by exposure to toxic compounds. Using immunological and molecular techniques the differential expression of specific proteins/RNAs and their activity can be studied. Among other proteins, c/ebp is involved in the regulation of transcription at the end of signal pathways. The protein is differentially expressed in rat lung cells and thus could be suitable for studying differential toxic effects in various lung cells. In humans, bronchoalveolar lavage (BAL) fluid from human volunteers can be readily obtained and examined after exposure to different chemical compounds. An increase in the percentage of CD3-positive cells (T-lymphocytes) was found after exposure to hydrogen fluoride. The number of certain cell types and cytokines may be used to estimate the degree of inflammatory reaction. In conclusion, the use of in vitro data including the use of specific, primary human lung cell types may contribute considerably to the quality of risk assessment, together with in vivo data from animals and man.

To elucidate cell differentiation in liver carcinogenesis, we have studied the CCAAT/enhancer-binding protein (C/EBP). C/EBP is a positive-acting transcription factor important for the maintenance of liver-specific functions. It is associated with differentiation and regarded as an anti-proliferative agent. We have studied the expression and localization of C/EBP during sequential rat liver carcinogenesis. Two-color immunohistochemistry and confocal laser scan microscopy demonstrated C/EBP in hepatocyte nuclei and preneoplastic liver lesions, but not in bile ducts, non-parenchymal cells or oval cells. Both western blotting and immunohistochemistry revealed down-regulation of C/EBP during normal regeneration and when regeneration was inhibited by the carcinogen, 2-acetylaminofluorene. A similar down-regulation was shown by western blotting in hepatocytes grown in culture. Our data suggest that the altered metabolic phenotype of preneoplastic liver lesions was not caused by a change in the expression of C/EBP. Furthermore, the data favor a hepatocyte derivation of preneoplastic liver lesions.

A series of halogenated propanes and propenes were studied for mutagenic effects in Salmonella typhimurium TA100 in the absence or presence of NADPH plus liver microsomes from phenobarbital-induced rats as an exogenous metabolism system. The cytotoxic and mutagenic effects of the halogenated propane 1,2-dibromo-3-chloropropane (DBCP) has previously been studied in our laboratories. These studies showed that metabolic activation of DBCP was required to exert its detrimental effects. All of the trihalogenated propane analogues were mutagenic when the microsomal activation system was included. The highest mutagenic activity was obtained with 1,2,3-tribromopropane, with approximately 50-fold higher activity than the least mutagenic trihalogenated propane, 1,2,3-trichloropropane. The order of mutagenicity was as follows: 1,2,3-tribromopropane > or = 1,2-dibromo- 3-chloropropane > 1,3-dibromo-2-chloropropane > or = 1,3-dichloro-2-bromopropane >> 1-bromo-2,3-dichloropropane > 1,2,3-trichloropropane. Compared to DBCP, the dihalogenated propanes were substantially less mutagenic. Only 1,2-dibromopropane was mutagenic and its mutagenic potential was approximately 1/30 of that of DBCP. In contrast to DBCP, 1,2-dibromopropane showed similar mutagenic activity with and without the addition of an activation system. The halogenated propenes 2,3-dibromopropene and 2-bromo-3-chloropropene were mutagenic to the bacteria both in the absence and presence of the activation system, whereas 2,3-dichloropropene did not show any mutagenic effect. The large differences in mutagenic potential between the various halogenated propanes and propenes are proposed to be due to the formation of different possible proximate and ultimate mutagenic metabolites resulting from the microsomal metabolism of the various halogenated propanes and propenes, and to differences in the rate of formation of the metabolites. Pathways are proposed for the formation of genotoxic metabolites of di- and trihalogenated propanes and dihalogenated propenes.

By use of an isolation procedure including centrifugal elutriation and density gradient centrifugation, relatively pure fractions of Clara cells and type II cells were obtained from rabbit lungs. These cells and alveolar macrophages isolated by lavage were exposed to methyl methanesulfonate (MMS), 1,2-dibromo-3-chloropropane (DBCP), 1-nitropyrene (1-NP), 2-nitrofluorene (2-NF), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK), N'-nitrosonornicotine (NNN), N-nitrosoheptamethyleneimine (NHMI) or phorbol 12-myristate 13-acetate (TPA). DNA damage measured as alkali-labile sites and/or single-strand breaks was then determined in the different lung cells by an automated alkaline elution system. The direct-acting compound MMS showed similar DNA-damaging effect in Clara cells, type II cells and alveolar macrophages. The nematocide DBCP, activated by both P450- and glutathione S-transferase(s)-dependent pathways, caused considerably less DNA damage in macrophages than in Clara or type II cells. Similar differences between the lung cells in induction of DNA damage as observed with DBCP were demonstrated after exposure to the activation-dependent nitrosamines NNK and NHMI and the tumor promoter TPA. The other test substances (1-NP, 2-NF, NNN) did not cause any marked DNA damage measured by the alkaline elution technique. These findings are in agreement with the known metabolic capacity of these cell types, indicating that Clara and type II cells are possible primary targets for lung toxic/carcinogenic compounds.

1,2-Dibromo-3-chloropropane (DBCP) and a number of halogenated propane analogs induced DNA damage in rat hepatocytes in vitro measured by an automated alkaline elution method. Short-term (2 hrs) cytotoxic effects of DBCP were not observed until the DBCP concentration exceeded 1 mM. The short-term cytotoxicity of all the DBCP analogs occurred in the same concentration range. Significant membrane damage, measured as cell detachment, was observed after extended exposure to lower concentrations of DBCP (100 microM) for 20 hrs. The relative, delayed cytotoxic effect of DBCP and analogs correlated with their ability to cause DNA damage. In general, the halogenated propanes with more bromines relative to chlorines were the more potent compounds. Propane analogs lacking the third halogen had little cytotoxic activity. The addition of the proposed specific poly(ADP-ribosyl)transferase inhibitor 3-aminobenzamide (3-ABA) protected against DBCP-induced cytotoxic effects and NAD+ depletion. However, 3-ABA also reduced DBCP-induced DNA damage, DBCP metabolic loss, and the formation of water soluble and covalently bound DBCP metabolites. Thus, 3-ABA may block DBCP-induced cell death by decreasing the formation of reactive DBCP-metabolites.

A series of halogenated propanes were studied for renal and testicular necrogenic effects in the rat and correlated to their ability to induce in vivo renal and testicular DNA damage and in vitro testicular DNA damage. 1,2-Dibromo-3-chloropropane (DBCP) and 1,2,3-tribromopropane were most potent in causing organ damage in both kidney and testes. Extensive necrosis was evident at 85 mumol/kg in kidney and at 170 mumol/kg in testis. The dibromomonochlorinated analogue 1,3-dibromo-2-chloropropane was less organ toxic than DBCP and 1,2,3-tribromopropane, but induced more organ damage than the dichloromonobrominated analogues 1-bromo-2,3-dichloropropane and 1,3-dichloro-2-bromopropane. Dihalogenated propanes were even less necrogenic. These observed differences in toxic potency between the halogenated propanes could not be explained by relative differences in tissue concentrations. The ability of the halogenated propanes to induce DNA damage in vivo correlated well with their ability to induce organ damage. However, DNA damage occurred at lower doses and at a shorter period of exposure than organ necrosis. This indicates that DNA damage might be an initial event in the development of organ necrosis by halogenated propanes in general. Further, testicular DNA damage induced by the halogenated propanes in vivo correlated well with the DNA damage observed in isolated testicular cells in vitro, showing that toxicity was due to in situ activation. The numbers, positions, and the types of halogen substituents appear to be important determinants in causing DNA damage and necrogenic effects.(ABSTRACT TRUNCATED AT 250 WORDS)

The poly(ADP-ribosyl)transferase inhibitor, 3-aminobenzamide (3-ABA), reduced morphological evidence of 1,2-dibromo-3-chloropropane (DBCP)-induced DNA damage determined by alkaline elution. The DBCP plasma, kidney, and testis tissue doses determined between 1 and 8 hr after a single intraperitoneal injection were somewhat higher with than without 3-ABA pretreatment. Furthermore, the amount of DBCP metabolites covalently bound to macromolecules was reduced to about 20-30 percent of control, indicating that 3-ABA may have an effect on the formation/detoxication of reactive DBCP metabolites. Inhibitors of replicative DNA synthesis such as hydroxyurea or stimulation of DNA replication by nephrectomy did not affect the cytotoxicity, neither did inhibitors of DNA repair such as beta-cytosine arabinoside and beta-lapachone.

The genotoxic potentials of N-nitrosoheptamethyleneimine (NHMI), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and N'-nitrosonornicotine (NNN) were studied in fresh preparations of Clara cells and type II cells isolated by centrifugal elutriation and density gradient centrifugation, and macrophages from rabbit lung. The activation of the compounds to bacterial mutagens was assayed in the Salmonella mutagenicity test using strains of TA 100 and TA 1530 preincubated with test chemicals and cells placed in chambers with nucleopore membranes to separate cells and bacteria. Unscheduled DNA synthesis was measured by incorporation of [3H]-thymidine in the cells after exposure to the compounds. NHMI, NNK and NNN were not activated to bacterial mutagens by Clara cells, type II cells or macrophages, presumably because the reactive metabolites generated were not released into the incubation medium. However, NHMI and NNK increased unscheduled DNA synthesis in Clara cells, and the highest repair activity was found after incubation with NNK. The effect of NNN was only marginal. This indicates that NHMI and NNK are genotoxic in the rabbit lung and that the Clara cells are involved in the metabolic activation of these compounds.

The irreversible binding of o,p'-DDD was examined in isolated lung cells, in lung microsomes and in vivo in male New Zealand White rabbits. Non-ciliated bronchiolar (Clara) cells had the highest capacity to bind o,p'-DDD, followed by alveolar type II cells. A fraction of mixed unidentified lung cells was also able to bind o,p'-DDD while no binding was observed in alveolar macrophages. The activation of o,p'-DDD was shown to be mediated by cytochrome P-450 in both lung microsomes and isolated lung cells. In vivo, the binding was preferentially localized in the lung alveolar and bronchiolar regions. The binding of o,p'-DDD observed in vivo may thus be caused by the capacity of several cell types to activate o,p'-DDD.

Species differences and mechanisms of 1,2-dibromo-3-chloropropane (DBCP) nephrotoxicity were investigated by studying DBCP renal necrosis and DNA damage, distribution and glutathione-dependent metabolism in rats, mice, hamsters and guinea pigs. Extensive renal tubular necrosis was observed in rats 48 hr after a single intraperitoneal administration (21-170 mumol/kg) of DBCP. Significantly less necrosis was found in mice and guinea pigs, whereas no renal damage was evident (less than 680 mumol/kg) in hamsters. The activation of DBCP to DNA damaging intermediates in vivo, as measured by alkaline elution of DNA isolated from kidney nuclei 60 min. after intraperitoneal injection of DBCP, was compared in all four species. Distinct DNA damage was detected in rats, mice and hamsters as early as 10 min. after administration of DBCP and within 30 min. in guinea pigs. Rats and guinea pigs showed similar sensitivity towards DBCP-induced DNA damage (extensive DNA damage greater than 21 mumol/kg DBCP), whereas in mice and hamsters a 10-50 times higher DBCP dose was needed to cause a similar degree of DNA damage. Renal DBCP concentrations at various time-points (20 min., 1, 3 and 8 hr) after intraperitoneal administration (85 mumol/kg) revealed that the initial (20 min.) DBCP concentration was substantially higher in rats and guinea pigs compared to the other two species. Furthermore, kidney elimination of DBCP occurred at a significantly lower rate in rats than in mice, hamsters and guinea pigs.(ABSTRACT TRUNCATED AT 250 WORDS)

The human testicular toxicant 1,2-dibromo-3-chloropropane (DBCP) was studied for the same end-point in 4 different species of laboratory animals. Marked necrosis and atrophy of the seminiferous epithelium were observed in rats and guinea pigs 10 days after a single i.p. administration of DBCP (170-340 mumol/kg), whereas significantly less damage was observed in hamsters and mice. The testicular concentrations of DBCP measured at various time-points after the i.p. injection of DBCP indicated that factors in addition to tissue concentration were of importance for the observed species differences in sensitivity towards DBCP-induced testicular damage. Also, there did not seem to be any direct correlation between DBCP-induced in vivo testicular toxicity and in vitro GSH-dependent dehalogenation, inasmuch as the rate of bromide release from DBCP with hamster testicular cytosol was as fast as that with rat cytosol. Testicular DNA damage, as determined by alkaline elution 60 min after in vivo administration of 170 mumol/kg DBCP, was observed only in rats and guinea pigs. Thus, induction of DNA damage correlates with the relative susceptibilities of the species towards DBCP-induced testicular necrosis. To further study species differences in testicular activation of DBCP to DNA-damaging intermediate(s), cells isolated from the testes of the 4 species were incubated with DBCP. Testicular cells from rats and guinea pigs were the only preparations developing substantial DNA damage after 60 min incubation with low concentrations of DBCP (5-50 microM). The findings indicate that rats are sensitive towards DBCP-induced testicular necrosis because rat testicular cells easily activate DBCP to a DNA-damaging intermediate(s). The relative high testicular DBCP concentration as well as the ability to activate DBCP may explain the sensitivity of guinea pigs towards DBCP-induced testicular toxicity.

Treatments known to alter P-450 activity and glutathione levels were used to elucidate the involvement of P-450 and glutathione S-transferase metabolism in 1,2-dibromo-3-chloropropane (DBCP) organ toxicity in the rat. Phenobarbital pretreatment abolished DBCP-induced renal necrosis, whereas it had only a small effect on initial renal DNA damage. The DBCP levels in plasma and tissues were markedly reduced by phenobarbital pretreatment. Perdeuterated DBCP had much higher plasma and tissue levels than protio-DBCP in phenobarbital-pretreated animals, but perdeuteration was without effect in uninduced animals. This indicates that P-450 metabolism of DBCP is of major importance only in phenobarbital-pretreated animals. In order to study the effects of decreased glutathione levels on renal distribution and toxicity, rats were pretreated with either diethyl maleate or buthionine sulfoximine. The DBCP levels in plasma and tissues showed transitory elevations after diethyl maleate and buthionine sulfoximine pretreatment compared to the control situation. Despite the fact that diethyl maleate and buthionine sulfoximine pretreatments are known to block DBCP-induced DNA damage in vitro, these pretreatments did not significantly alter DBCP-induced renal necrosis nor DNA damage. Thus, a role for glutathione conjugation in DBCP-induced in vivo renal toxicity could not be established in the present study.

In vitro bromide release and in vivo glutathione (GSH) depletion in rat liver, kidney and testis by 1,2-dibromo-3-chloropropane (DBCP) and selectively methylated and deuterated DBCP analogs were studied. With liver microsomes from phenobarbital-pretreated rats the bromide release from the C1-C3-D4- and the perdeuterated DBCP analogs were 54% and 26% of that of DBCP, respectively. Inhibitors of P-450 reduced the bromide release to 10-20% of that without additions. This correlated with the effects of deuterium substitution and additions of P-450 inhibitors on DBCP-induced bacterial mutagenicity as reported elsewhere by this laboratory. To study the importance of GSH-dependent metabolism in DBCP toxicity, bromide release was assayed in cytosolic preparations using methylated analogs of DBCP. With the C1-methyl-derivative, bromide release was markedly reduced compared to that with DBCP in cytosols from liver, kidney and testis. A similar reduction in in vivo nephrotoxicity and testicular damage has recently been reported. The obtained correlation between in vitro GSH-dependent metabolism of methylated DBCP analogs and their in vivo organ damaging potential, points to an involvement of GSH-dependent metabolism in DBCP-induced in vivo toxicity. Both DBCP and the methylated analogs (360 mumol/kg i.p.) depleted the GSH levels in liver after 1 and 3 h and in kidney after 1 h, whereas in the testis no significant depletion of GSH was obtained. As kidney and testis are reported to be the primary target organs for DBCP, there was an apparent lack of correlation between tissue depletion of GSH and organ toxicity.

Swelling of epithelial cells and reduction of ciliary activity in mouse trachea organ culture occurred after incubation for 4 h with a rather low concentration of cadmium acetate (10 microM). Specific inhibitors of ion transport (Na+, K+, Cl-) such as furosemide, amiloride and ouabain did not mimic, abolish or increase the toxic effects induced by cadmium acetate. Exposure to cadmium acetate had no significant effect on electrolyte uptake (22Na+ and 86Rb+). These results suggest that the swelling of epithelial cells induced by cadmium acetate is not due to an osmotic swelling from an accumulation of electrolytes. Ba2+, known to have several biological properties in common with Ca2+, and to influence basolateral K+ flux, counteracted the toxic effects of cadmium acetate, whereas a more rapid and extensive swelling occurred with cadmium acetate in a medium without Ca2+. No effect on the uptake of 109Cd2+ was found with barium chloride, whereas in a medium without Ca2+ the Cd2+ uptake increased by 47%. Trifluoperazine (100 microM), a drug which in vitro binds tightly to calmodulin, imitated the toxic effects of 10 microM cadmium acetate. The combination of 10 microM cadmium acetate and 100 microM trifluoperazine resulted in an additive toxic effect. A possible mechanism for the cadmium acetate-induced swelling and inhibition of ciliary activity could, thus, be a disturbance of the regulatory activity of calmodulin.

The effects of cadmium acetate and sodium selenite in mouse trachea organ culture have been studied separately and in combination. Ciliary activity, morphology, rate of total protein and glycoconjugate (i.e. glycoprotein and proteoglycan) synthesis/secretion and ATP content were investigated. Exposure to 10 microM cadmium acetate or 2000 microM sodium selenite resulted in a complete cessation of ciliary activity within 5 h. With cadmium acetate also a swelling of epithelial cells was observed. Sodium selenite (250-2000 microM) delayed by 2-3 h the inhibitory effect of cadmium acetate (5-20 microM) on ciliary activity. The rate of protein synthesis, as determined by incorporation of [3H]proline, was reduced by 13% and 44% at exposure for 4 h at 37 degrees C to 250 microM and 500 microM sodium selenite respectively, the effect being partly abolished by cadmium acetate. With 5 microM and 10 microM cadmium acetate the rate of glycoconjugate synthesis, as measured by incorporation of [3H]glucosamine, increased by 50% and 69%, respectively, after incubation for 4 h. This increase was partly reduced by sodium selenite. Neither cadmium acetate nor sodium selenite had any effect on the rate of total protein or glycoconjugate secretion. The ATP content in trachea rings was reduced by 48% and 54% after incubation for 4 h with 250 microM and 500 microM sodium selenite, respectively. No significant effect of cadmium acetate was found on ATP content. An antagonistic effect of sodium selenite and cadmium acetate in mouse trachea organ culture is suggested from the present experiments.

Trachea from albino mice were cut transversely into nearly identical rings and incubated in medium 199 with Hanks salts and HEPES buffer at 37 degrees C. Sodium selenite at 0.5-5 mM depressed the ciliary activity. With 1 and 5 mM sodium selenite, a 50% reduction in the activity index was observed after approximately 5 and 1.5 h, respectively. The ATP content in trachea rings was reduced with 0.05-5 mM sodium selenite, and increasing concentrations gave decreasing amount of ATP after incubation for 4 and 21 h. The rate of protein synthesis as determined by incorporation of radioactive leucine was reduced with 0.5 and 2 mM sodium selenite. The synthesis was reduced quickly by 2 mM sodium selenite, which gave a 30% reduction after incubation for 1 h. It seems that the ATP levels may be used as the most sensitive indication of sodium selenite toxicity in mouse trachea.