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Notes: Abstract Groups of male C57Bl and CD-1 mice were exposed to benzene via inhalation using two different exposure protocols. One protocol consisted of repetitive week-long exposures to 300 ppm benzene (6 h/d×5 d/wk) interrupted by 2 weeks of non-exposure. The exposure pattern (1 week of exposure followed by 2 weeks of non-exposure) was continued until the death of the last exposed animal. The second protocol consisted of exposures to 1200 ppm benzene (6 h/d×5 d/wk) for 10 weeks. Exposures were then terminated and the animals allowed to live out their lives. For each protocol, appropriate age-matched control mice received comparable exposures to filtered, conditioned air. The discontinuous exposure patterns mimic the patterns of exposure often encountered in the workplace and, in addition, prolong the survival of exposed animals so as to maximize potential tumorigenic responses. Both exposure protocols were markedly hematotoxic to both mouse strains as measured by peripheral blood counts. Both strains of mice responded to the intermittent 300 ppm benzene exposures with elevated incidences of malignant tumors. Particularly noteworthy was a 35% incidence of zymbal gland tumors in the C57Bl mice. In contrast, only the CD−1 mice responded to the 1200 ppm benzene exposures delivered over 10 weeks with elevated tumor incidences. A 46% incidence of lung adenoma was particularly striking in these mice. Neither of the benzene exposure protocols induced elevated incidences of leukemia/lymphoma in either strain. These studies demonstrate that discontinuous exposures to benzene are tumorigenic and that a lifetime exposure to benzene, even if delivered at a lower concentration and in an intermittent exposure pattern, is more tumorigenic than a short-term exposure to benzene.

Notes: Abstract A new inhalation exposure system has been developed which allows the determination of inhaled doses of vapors and gases by laboratory rats. The system consists of saran bags connected to head-only exposure cylinders via one-way valves. One bag serves as the source of contaminant and another receives expired air. The exposure cylinders also serve as whole body plethysmographs. Up to three rats can be exposed concurrently to the same concentration of test material. The construction of the system and its use for inhalation exposures to a direct-acting radiolabeled carcinogen are described.

Notes: Abstract It has long been recognized that benzene exposure produces disparate toxic responses among different species or even among different strains within the same species. There is ample evidence that species- or strain-dependent differences in metabolic activity correlate with the disparate responses to benzene. However, bone marrow cells (the putative targets of benzene toxicity) may also exhibit species- or strain-dependent differences in susceptibility to the toxic effects of benzene. To investigate this hypothesis, two sets of companion experiments were performed. First, two strains of mice, Swiss Webster (SW) and C57B1/6J (C57), were exposed to 300 ppm benzene via inhalation and the effects of the exposures were determined on bone marrow cellularity and the development of bone marrow CFU-e (Colony Forming Unit-erythroid, an early red cell progenitor). Second, bone marrow cells from the same strains were exposed in vitro to five known benzene metabolites (1,4 benzoquinone, catechol, hydroquinone, muconic acid, and phenol) individually and in binary combinations. Benzene exposure, in vivo, reduced bone marrow cellularity and the development of CFU-e in both strains; however, reductions in both these endpoints were more severe in the SW strain. When bone marrow cells from the two strains were exposed in vitro to the five benzene metabolites individually, benzoquinone, hydroquinone, and catechol reduced the numbers of CFU-e in both strains in dose-dependent responses, phenol weakly reduced the numbers of the C57 CFU-e only and in a non-dose-dependent manner, and muconic acid was without effect on cells from either strain. Only benzoquinone and hydroquinone exhibited differential responses to CFU-e from the two strains and both of these metabolites were more toxic to SW cells than to C57 cells. Six of the ten possible binary mixtures of metabolites were differentially toxic to the CFU-e from the two strains and five of these mixtures were more toxic to SW cells than to C57 cells. Thus, SW mice were more susceptible to the toxic effects of inhaled benzene and their bone marrow cells were more severely affected by in vitro exposure to benzene metabolites. The binary combinations containing phenol produced little or no enhancement of the toxic effects of the non-phenol metabolites. The weak toxic response induced by phenol, whether delivered alone or in binary mixtures, suggests that little metabolism occurred during the 48 h of the in vitro exposures since benzoquinone and hydroquinone, which were clearly toxic when added to the CFU-e culture system, are formed by further metabolic oxidation of phenol. Thus, strain-dependent differential metabolism appeared to play a minimal role in the disparate toxicity observed in the in vitro studies, implying that the diverse responses were due to inherent differences in the susceptibilities of the CFU-e to the toxic action of the benzene metabolites.

Notes: Abstract Studies have been performed to investigate the effects of combined in vivo exposures to inhaled benzene and ingested ethanol on the earliest known murine erythropoietic precursor cells, the Burst Forming Unit — Erythroid (BFU-E) and the Colony Forming Unit — Erythroid (CFU-E). Previously we had determined that murine erythropoietic cell populations were particularly susceptible to combined benzene + ethanol treatments. The most striking example of erythropoietic disruption was the transient appearance of large numbers of nucleated red cells (normoblasts) in the circulating blood. In the present studies, male C57B1/6 mice were exposed to 300 ppm benzene via inhalation for 6 h/d×5 d/wk×9 wks. Groups of mice were also exposed to 5% ethanol in the drinking water 4 d/wk×9 wks. Appropriate controls were also maintained. The hematological assays were performed after 1, 4, and 9 weeks of exposure. After 4 weeks of exposure large numbers of normoblasts appeared in the circulating blood of mice exposed to benzene + ethanol. However, there were no corresponding increases in the numbers of the earliest erythroid progenitor cells in the bone marrow. There were, however, marked increases in the numbers of these cells in the spleen. Previous work in this laboratory had confirmed that the marrow was the source of circulating normoblasts among animals exposed to benzene + ethanol. We conclude, therefore, that circulating normoblasts appear in the peripheral blood because of changes in the bone marrow microenvironment rather than as a consequence of increased erythropoietic proliferation in the marrow.

Notes: Abstract. Benzene is a well known hematotoxicant which induces hematopoietic dyscrasias of varying intensities in different individuals and even in different strains of the same experimental animal species. Although there is ample evidence that diverse responses to benzene are related to differences in benzene metabolism, we have recently provided evidence implicating differences in host target cell susceptibility to these diverse responses to benzene. The present study extends our previous work and concerns strain-specific differences in marrow progenitor cells that survive benzene exposure. Two mouse strains (Swiss-Webster and C57Bl/6J) which respond to benzene exposure with different intensities of bone marrow cytotoxicity were used. Bone marrow cells from benzene-exposed and untreated mice were cultured with one of five benzene metabolites: 1,4-benzoquinone (BQ), catechol (C), hydroquinone (HQ), muconic acid (MA) or phenol (P) and the abilities of these cells to produce erythroid (CFU-e) or granulocyte/macrophage colonies (GM-CFU-c) were assessed. In both strains, marrow cells isolated from benzene-exposed mice showed a higher percentage of plated CFU-e surviving culture with BQ, HQ or MA than marrow cells isolated from control mice. In contrast, both strains of benzene-exposed mice displayed decreased percentages of plated CFU-e surviving culture with catechol than cells isolated from control mice. Only one condition (the culturing of cells with HQ under GM-CFU-c forming conditions) showed any strain-specific difference in plating efficiency. In all, 20 possible combinations of benzene metabolites and cell types were examined (5 metabolites × 2 progenitor cell types × 2 strains). With seven of these combinations, the colony-forming efficiencies were higher for plated cells isolated from benzene-exposed mice than from untreated mice. With three combinations, the colony-forming efficiencies were lower for cells from benzene-exposed mice, and for ten combinations, there were no changes in plating efficiencies. Possible mechanisms for an acquired resistance to the toxicities of benzene metabolites were explored by measuring the concentrations of hepatic and bone marrow sulfhydryl (SH) groups in cells isolated from benzene-exposed and untreated mice. In both strains, benzene exposure induced no changes in hepatic SH concentrations, but the SH content of bone marrow was more than doubled after benzene exposure in both strains. These results suggest that a fraction of hematopoietic progenitor cells are able to survive severe benzene exposure and produce progeny because of a marked increase in marrow SH groups which react with electrophilic benzene metabolites. Moreover, this protective mechanism occurs in two mouse strains with differing susceptibilities to benzene.

Notes: Abstract Because chronic benzene exposure is associated with acute myeloblastic leukemia and other myeloproliferative disorders, we sought to determine whether short-term benzene exposure provides a growth advantage for granulopoietic elements over erythropoietic elements. Groups of male DBA/2J mice were exposed to 0, 10, 30, or 100 ppm benzene (6 h/day for 5 days). One day and 5 days after the benzene exposures, the numbers of the two most primitive erythroid progenitor cells (BFU-E and CFU-E) and the numbers of the most primitive granulocytic progenitor cells (GM-CFU-C) were assessed. Additional groups of mice were given hemolytic doses of phenylhydrazine (PHZ) during the 5 days of benzene exposure, while other groups of mice were given PHZ during the 5 days of recovery from benzene exposure. These experiments were designed to determine the effects of benzene exposure on progenitor cell numbers during periods of markedly heightened erythropoiesis. The results demonstrate that short-term benzene exposure does induce a growth advantage for granulocytic cells in both the bone marrow and spleen of exposed mice. Moreover, a benzene-induced shift toward granulopoiesis is observed even in those mice treated with a powerful erythropoietic stimulus. These effects disappear 5 days after cessation of benzene exposure in the bone marrow but persist in the spleen of mice treated with phenylhydrazine.

Notes: Abstract In previous work, we determined that granulocytic (CFU-GM) and erythroid (CFU-E) progenitor cell populations exhibited disparate responses to short-term benzene exposures. We now report on work investigating possible mechanisms for these observed disparate responses. Mice were exposed to either air or 10 ppm benzene for 6 h/d X 5 d. Immediately after the last exposure, mice were injected, i. v., with either saline or hydroxyurea (HU). The dose of HU was sufficient to kill hematopoietic cells in or near S-phase of the cell cycle and sufficient to synchronize the surviving populations of hematopoietic cells. Three days after benzene exposure, CFU-E numbers had declined to 50% of control values while CFU-GM numbers were equal to control values at this time. The benzene exposures were sufficient to double the percentage of CFU-E in S-phase but produced no such increase among CFU-GM. During 3 days of recovery from benzene exposure and HU treatment, the CFU-E population expanded 30-fold while the CFU-GM population expanded less than 3-fold. Following benzene exposure and HU treatment, both progenitor cells produced elevated numbers of their respective progeny. When CFU-E from benzene-exposed mice were cultured with varying concentrations of erythropoietin (EPO), the response at maximal EPO concentration was 66% of the response by control CFU-E. This strongly suggests that the CFU-E populations from benzene-exposed mice had been depleted of cells in or near S-phase. The results indicate that CFU-GM respond to low-level benzene exposure by increasing their rate of differentiation but not their rate of proliferation, while CFU-E respond by increasing both their rates of differentiation and proliferation. We speculate that it is the increase in CFU-E proliferation that renders these cells more susceptible to benzene than their granulocytic counterparts, especially those CFU-E at or near the S-phase of the cell cycle.