Differences between rats and mice in the immunosuppressive activity of 2-methoxyethanol and 2-methoxyacetic acid

Early toxicology signal generation in the mouse

The rat has been the preferred rodent toxicology species since before regulatory requirements have been in place, and there exists in the pharmaceutical industry and the regulatory agencies a significant amount of historical data for the rat. The resulting experience base with the rat makes the possibility of replacing it with the mouse for regulated toxicology studies untenable for all but the most extreme circumstances. However, toxicologists are very familiar with the mouse as a model for chronic carcinogenicity studies, and there exist multiple preclinical mouse models of disease. The authors evaluated the use of the mouse for early in vivo toxicology signal generation and prioritization of small molecule lead compounds prior to nomination of a development candidate. In five-day oral gavage studies with three test agents in the mouse, the authors were able to identify the same dose-limiting toxicities as those identified in the rat, including examples of compound-mediated hemolysis as well as microscopic lesions in the alimentary canal, kidney, and pancreas. Performing early signal generation studies in the mouse allows for earlier assessment of the safety liabilities of small molecules, requires significantly less compound, and allows evaluation of more compounds earlier in the project's life cycle.

Testicular Toxicity of Candidate Fuel Additive 1,6-Dimethoxyhexane: Comparison with Several Similar Aliphatic Ethers

Previous studies of the toxicity of candidate fuel additives identified severe testicular toxicity in animals exposed to 1,6-dimethoxyhexane (DMH). A series of studies were conducted to characterize the effects of DMH on spermatogenesis and to compare the effects of DMH with responses to structural similar aliphatic ethers. In the first study, sexually mature male rats were administered a single dose (600 mg/kg) of DMH, and subsets of animals were sampled at intervals post exposure (PE). Both testis and thymus weight declined steadily after DMH exposure, both being significantly lower than control by 7 days PE. Treatment with DMH led, at 24 to 48 h PE, to an increase in dying primary spermatocytes in seminiferous tubule stages I-IV and stages XII-XIV, but not intervening stages. The affected cohort of germ cells was seen progressing through the developmental sequence of spermatogenesis as numbers of dying cells returned to control levels by 7 days PE, coincident with a significant decline in the proportion of round spermatids among germ cells as determined by flow cytometry. Resolution of round spermatids to control levels by day 21 PE coincided with a reduction in condensed spermatids (homogenization-resistant spermatid nuclei) and was followed at 28 days PE by a significant reduction in cauda epididymal sperm counts. Further studies of repeated exposures to DMH (200 mg.kg(-1).day(-1), 5 days per week for 4 weeks) confirmed the significant testis toxicity of this material. In contrast, similar treatment with any of a variety of structurally similar aliphatic ethers had little or no impact on testis function. Methoxyacetic acid, previously shown to cause rapid death of some meiotic germ cell stages, was found at high concentrations in the urine of DMH-treated rats but not in rats treated with other ethers, suggesting that DMH exerts its testis toxicity via metabolism to this substance. These results demonstrate that DMH selectively deletes germ cells from the testis At the very early or very late pachytene, diplotene, or M-phase spermatocyte stages, possibly through conversion to MAA.

Short-term oral toxicity of butyl ether, ethyl hexyl ether, methyl heptyl ether and 1,6-dimethoxyhexane in male rats and the role of 2-methoxyacetic acid

A 4-week oral study was conducted in male rats to characterize and compare the toxicity of four aliphatic ethers (butyl ether, BE; ethyl hexyl ether, EHxE; methyl heptyl ether, MHpE; and 1,6-dimethoxyhexane, DMH) which have been proposed as high-cetane diesel additives. Male Sprague-Dawley rats (280+/-20 g) were divided into groups of seven animals each and were administered by gavage low (2mg/kg body weight), medium (20mg/kg) or high (200mg/kg) doses of BE, EHxE, or MHpE, 5 days per week for 4 weeks. Another group of animals was administered DMH at 200mg/kg while the control group received the vehicle (corn oil at 1 ml/100g bw) only. At the end of the treatment period, relative testis weights and thymus weights were significantly decreased in the DMH group but not in animals receiving BE, EHxE, or MHpE. Microscopic examination revealed degeneration of the seminiferous tubules and reduction of sperm density in the epididymides in the DMH treatment group. Urinary creatine/creatinine ratio, a sensitive indicator of testicular damage, was markedly elevated in the DMH treated animals but not in those treated with BE, EHxE, or MHpE. In the bone marrow, DMH caused mild dyserythropoiesis and dysthrombopoiesis, while BE, EHxE, and MHpE produced mild increases in granulocytes and myelocyte/erythrocyte ratio. All four ethers at 200mg/kg caused mild histological changes in the thyroid but no significant modulation in the circulating thyroxin (T4) or triiodothyronine (T3) levels. All four ethers produced hepatic effects at 200mg/kg consisting of mild, adaptive histological changes, increased urinary ascorbic acid output, and elevation in the activities of one or more xenobiotic metabolizing enzymes (benzyloxyresorufin-O-dealkylase, UDP-glucuronosyltransferase, glutathione-S-transferases). The level of 2-methoxyacetic acid (MAA), a known testicular and developmental toxin, was significantly increased in the urine and plasma of animals treated with DMH but not in those administered the high dose BE, EHxE, or MHpE. Amomg the individual rats treated with DMH, the MAA level appeared to correlate with the severity of toxicity such as testicular and thymic weights, and urinary creatine/creatinine ratio. It is concluded that BE, EHxE, and MHpE differed from DMH in that they did not produce testicular or thymic toxicity. All four ethers at high dose caused changes to the thyroid, liver and bone marrows that were mild and adaptive in nature. MAA appeared to be the proximal toxicant in DMH treated animals but the route by which DMH is metabolized to MAA remains to be elucidated.

Topical exposure to 2-butoxyethanol alters immune responses in female BALB/c mice

Effects on immune parameters following topical exposure to 2-butoxyethanol (BE) in mice are reported in the present study. The objective was to determine whether subacute topical exposure to BE can modulate functional immune responses and/or nonspecific immune parameters such as lymphoid organ weight and cellularity. Female BALB/c mice were topically exposed to vehicle or BE at concentrations of 100, 500, 1,000, and 1,500 mg BE/kg/day for 4 consecutive days. Assessment of immune parameters began 24 hours after the final dose. No effects were observed at any of the BE concentrations on thymus cellularity or thymus to body weight ratio. A significant increase in spleen cellularity and spleen to body weight ratio was observed at 1,500 mg BE/kg/day. Topical BE exposure significantly reduced the splenic T cell proliferative response to concanavalin A (Con A) and the mixed lymphocyte response (MLR) to allogeneic antigen. No significant effect was observed in the splenic B cell proliferative response to lipopolysaccharide (LPS), nor was there an effect on the in vitro primary antibody response to sheep red blood cells (SRBCs). No significant alteration occurred in either splenocyte cytotoxic T lymphocyte (CTL) activity or natural killer (NK) cell activity following topical BE exposure. This study suggests that topical exposure to BE may suppress some aspects of T cell immunity but does not affect B cell immunity.

Toxicity review of ethylene glycol monomethyl ether and its acetate ester

Ethylene glycol monomethyl ether (EGME) and its acetate ester (EGMEA) are highly flammable, colorless, moderately volatile liquids with very good solubility properties. They are used in paints, lacquers, stains, inks and surface coatings, silk-screen printing, photographic and photo lithographic processes, for example, in the semiconductor industry, textile and leather finishing, production of food-contact plastics, and as an antiicing additive in hydraulic fluids and jet fuel. EGME and EGMEA are efficiently absorbed by inhalation as well as via dermal penetration. Dermal absorption may contribute substantially to the total uptake following skin contact with liquids or vapours containing EGME or EGMEA. EGMEA is rapidly converted to EGME in the body and the two substances are equally toxic in animals. Therefore, the two substances should be considered as equally hazardous to man. Effects on peripheral blood, testes, and sperm have been reported at occupational exposure levels ranging between 0.4 and 10 ppm EGME in air, and with additional, possibly substantial, dermal exposure. Severe malformations and disturbed hematopoiesis have been linked with exposure to EGME and EGMEA at unknown, probably high, levels. Embryonic deaths in monkeys and impaired spermatogenesis in rabbits have been reported after daily oral doses of 12 and 25 mg per kg body weight, respectively. In several studies, increased frequency of spontaneous abortions, disturbed menstrual cycle, and subfertility have been demonstrated in women working in the semiconductor industry. The contribution of EGME in relation to other exposure factors in the semiconductor industry is unclear.

Experimental studies on immunosuppression: how do they predict for man?

The ultimate goal of any animal model in immunotoxicity testing is that it be a sensitive predictor of xenobiotic-induced immune dysfunction in humans. Such models should be capable of identifying the target(s) within the immune system affected by the xenobiotic. In particular the tier testing models have been successfully used to identify and characterize a variety of different immunotoxicants in animals as it pertains to immunosuppression and reduced resistance to infectious diseases. These tier models in mice and rats have been validated in interlaboratory studies. Although these protocols were designed for studies of rats and mice, some have been applied successfully for studying immunotoxicity in other animal species, including non-human primates. A great amount of data has been generated by the application of these models, which demonstrate that xenobiotics alter the immune system of animals. In man, the database on chemical-induced immunosuppression is limited, as the use of markers of immunotoxicity has received little attention in clinical and epidemiological studies. Such studies have not been performed frequently, and their interpretation often does not permit unequivocal conclusions to be drawn, due for instance to the presence of confounding factors and the uncontrolled nature of exposure. Also, testing possibilities in humans are limited and immune function changes by chemical exposure are often subtle. In humans, a number of agents have been shown to have immunosuppressive properties (including PCBs, PCDDs, PCDFs, oxidant gases, and ultraviolet radiation), but the strongest evidence stems from the clinical use of immunosuppressant drugs in transplant patients. These human data do in general terms confirm the data gained with experimental animals. Immunotoxicity assessment in rodents therefore adequately forms the basis for human risk assessment. Knowledge on the predictability of these animal models and immune assays can be further improved by comparison of the human and animal data obtained in the development of drugs.

The role of metabolism in 2-methoxyethanol-induced suppression of in vitro polyclonal antibody responses by rat and mouse lymphocytes

Previous studies from this laboratory have shown that the glycol ether 2-methoxyethanol (ME) produces immunosuppression in the rat but not in the mouse. To investigate possible mechanisms for this species difference in ME-induced immunotoxicity, the effects of ME and its metabolites, 2-methoxyacetic acid (MAA) and 2-methoxyacetaldehyde (MAAD), on in vitro polyclonal antibody responses by Fisher 344 rat and B6C3F1 mouse lymphocytes, were studied. MAAD and MAA suppressed IgM and IgG production by both mouse and rat lymphocytes at non-cytotoxic doses. However, ME had no effect on antibody production by either mouse or rat lymphocytes. Lower concentrations of MAA suppressed rat lymphocyte IgM and IgG production (at 0.5 and 1.0 mM MAA, respectively) compared with mouse lymphocytes (2.0 mM MAA). IgM and IgG production by both rat and mouse lymphocytes was suppressed at comparable concentrations of MAAD (0.3 mM MAAD). The role that metabolism of ME to its immunosuppressive forms plays in this in vitro suppression was demonstrated using hepatocyte-lymphocyte co-cultures. IgM production by both mouse and rat lymphocytes was suppressed at a lower concentration of ME following co-culture with mouse (12.5 mM ME) versus rat (25 and 50 mM ME) hepatocytes. These in vitro results indicate that rat lymphocytes are more sensitive to MAA than are mouse lymphocytes and that mouse hepatocytes have a greater capacity to metabolize ME to its immunosuppressive metabolites than do rat hepatocytes. In addition, MAAD is more immunotoxic than MAA, suggesting that this metabolite may be the proximate immunotoxicant. These observation may partially explain the species differences in ME-induced immunosuppression in vivo.

Repeated high dose oral exposure or continuous subcutaneous infusion of 2-methoxyacetic acid does not suppress humoral immunity in the mouse

2-Methoxyethanol (ME) has been shown to be immunosuppressive in rats but not mice, with oxidation of ME to 2-methoxyacetic acid (MAA) being a prerequisite for immunosuppression. MAA is more rapidly cleared by mice than rats, consequently this study was designed to determine if increasing the bioavailability of MAA in mice might play a role in this species difference. Female B6C3F1 mice were given MAA by oral multiple daily high doses or by continuous subcutaneous infusion via mini-osmotic pumps. Humoral immunity was evaluated in MAA-exposed mice using the plaque-forming cell (PFC) response to either sheep red blood cells (SRBC) or trinitrophenyl-lipopolysaccharide (TNP-LPS). Female F344 rats were also used to compare the effects of multiple daily MAA exposure on these humoral immune responses. Rats and mice were dosed orally twice a day for 4 days by gavage with MAA at dosages ranging from 40-320 mg/kg/day and 240-1920 mg/kg/day, respectively. All animals were immunized on the first day of dosing and body and lymphoid organ weights and PFC responses to SRBC or TNP-LPS were evaluated 4 days later. While body weights in rats were unaffected, thymus weights were reduced at all dosages of MAA and spleen weights were reduced at 160 or 320 mg/kg/day. PFC responses to SRBC and TNP-LPS were suppressed in rats at dosages of 160 and 320 mg/kg/day. In contrast, thymus weights of mice were reduced only at 960 mg/kg/day or greater, with no effect on spleen or body weights. Furthermore, neither the PFC response to SRBC nor the response to TNP-LPS was suppressed in mice exposed to any oral dosage of MAA. In the continuous infusion study, mice were subcutaneously implanted with mini-osmotic pumps containing MAA which was delivered at 840 mg/kg/day over a 7-day period. Continuous exposure to MAA via mini-osmotic pumps did not suppress the PFC response to either SRBC or TNP-LPS, but rather significantly enhanced the response to TNP-LPS. These results indicate that mice are insensitive to MAA even at the high dosages given as a bolus or continuously over 1 week. The data further support earlier work, which suggested that the observed difference between rats and mice for MAA-induced immunosuppression appears to be unrelated to the availability of MAA to target lymphoid tissue in these rodent species.

Species differences in testicular and hepatic biotransformation of 2-methoxyethanol

Biotransformation of 2-methoxyethanol (2-ME) by alcohol and aldehyde dehydrogenases is an established factor in the toxicity of this useful solvent. Little is known about potential capacity for 2-ME biotransformation by testis or other target tissues. We detected appreciable capacity for 2-ME biotransformation by alcohol dehydrogenase in testes from Sprague-Dawley rats. However, kinetic analysis showed a 6-fold lower affinity for 2-ME by alcohol dehydrogenase of testis compared to liver. 2-ME biotransformation was also detected in testes from Wistar rats and one strain of mice but not in testes from hamsters, guinea pigs, rabbits, dogs, cats or humans. Testes from all these species readily converted the aldehyde metabolite of 2-ME to 2-methoxyacetic acid. Hepatic capacities for 2-ME biotransformation by alcohol dehydrogenase varied from 22 to 2.5 mumol/mg prot/min with a species rank order of: hamsters >> rats = mice > guinea pigs = rabbits. There was no consistent concordance between activities for 2-ME versus ethanol, the prototype substrate for alcohol dehydrogenase, which could reflect substrate preferences of different isozymes. Species differences between rats and hamsters were also found for testicular and hepatic biotransformation of the glycol ethers, 2-ethoxyethanol and 2-butoxyethanol. Although species differences in capacity for 2-ME biotransformation were found, the observations do not provide an explanation for reported species and strain differences in susceptibility to 2-ME toxicity.

Immunotoxicological investigation using pharmaceutical drugs. In vitro evaluation of immune effects using rodent or human immune cells

In order to evaluate the relevance of in vitro methods for immunotoxicity assessment, the effects of pharmaceutical drugs on lymphoproliferative and cytotoxic functions of mouse splenocytes and human peripheral blood mononuclear cells (hPBMC) were studied. A comparison of sensitivity of immune cells from different origins to an in vitro exposure to different xenobiotics was performed using non-immunosuppressive (cimetidine and furosemide) and immunosuppressive (azathioprine (AZA), cyclosporine A (CSA), and dexamethasone (DEX)) drugs. For CSA, sensitivity of both rat and mouse splenocytes following in vitro exposure was compared to the one of hPBMC. Immune function tests included lymphoproliferative response to mitogenic lectins (concanavalin A (Con A) and phytohemagglutinin (PHA-P)) or to allogeneic cells (mixed leukocyte response (MLR)) and cytotoxicity assays (cytotoxic-T lymphocyte (CTL) and natural killer (NK) cell-mediated cytolysis). Additionally, to evaluate how well in vitro assays represent the in vivo situation, a comparison of the effect of cyclosporine A on the same immune function tests following in vivo or in vitro exposure was performed. The data obtained show numerous similarities in the effects observed following in vitro exposure of rodent or human cells to the drugs and a very similar sensitivity of rat and mouse cells to CSA in vitro. Discrepancies between human and rodent cells such as lymphoproliferative response to PHA-P following exposure to DEX or sensitivity of CTL-mediated cytolysis to CSA do exist. In vitro assays were very representative of the in vivo situation, both in the rat and in the mouse, following CSA exposure, except for NK cell activity in the rat. These data show the usefulness of in vitro systems for immunotoxicity assessment. They allow direct comparison of rodent and human systems, and could be representative, for drugs altering specifically the immune system like CSA does, of the in vivo situation.

Immune parameters are affected differently after cyclosporine A exposure in Fischer 344 rats and B6C3F1 mice: implications for immunotoxicology

Knowledge of interspecies differences, commonly evaluated in other disciplines such as carcinogenesis, is a prerequisite for an appropriate assessment of immunotoxicological risks. The purpose of this study was to assess interspecies differences following exposure of Fischer 344 rats and B6C3F1 mice to cyclosporine A. These animals were exposed daily to cyclosporine A by oral gavage at 0, 5, 10, 25 mg/kg/day for 14 consecutive days. The results showed that splenocytes lymphoproliferation in response to concanavalin A or phytohemagglutinin, and IgM antibody-forming cells to sheep red blood cells, were affected in both species. Cytotoxic T-lymphocyte activity and mixed lymphocyte response were significantly inhibited in the rat following cyclosporine A exposure while they remained unaffected in the mouse. In contrast, natural killer cell activity was significantly depressed in the B6C3F1 mouse but not in the Fischer 344 rat. The discrepancies between the two species in cytotoxic T-lymphocyte activity and mixed lymphocyte response assays could partially be explained by the constantly higher blood level of cyclosporine A in the rat than in the mouse. When these tests were performed using rat and mouse splenocytes exposed to cyclosporin A in vitro (10(-9) to 10(-5) M) it was possible to correlate in vivo and in vitro data for concanavalin A- and phytohemagglutinin-induced lymphoproliferation and for cytotoxic T-lymphocyte activity but not for mixed lymphocyte response. Natural killer activity was 10-fold more sensitive in mice than in rats in vitro but these results did not clarify the in vivo difference. In conclusion, these results emphasize that the utilization of more than one species should be considered when assessing immunotoxicity.

Effects of in vitro exposure to ultraviolet radiation on the functional activity of lymphocytes, with emphasis on susceptibility of different species

In this study lymphocytes from blood and/or spleen of different species (rat, mouse, human) were exposed to different doses of ultraviolet radiation (UVR). The functional activity of these lymphocytes was determined using assays for mitogen proliferation and the mixed lymphocyte response (MLR). These experiments demonstrated that in vitro exposure to UVR causes a dose-dependent decrease of the MLR activity of the irradiated lymphocytes. Viability of lymphocytes and mitogen proliferation responses were also decreased by UVR exposure but less severe in comparison to the MLR. Lymphocytes of rats seem to be more sensitive to UVR as compared to lymphocytes of mice and humans.

Species and strain comparisons of immunosuppression by 2-methoxyethanol and 2-methoxyacetic acid

2-Methoxyethanol (ME) and its principal metabolite 2-methoxyacetic acid (MAA) have been shown in our laboratory to be immunosuppressive in male Fischer 344 rats. In this study several strains of 12-week-old female rats and mice were used to compare the immunosuppressive activity of equimolar concentrations of ME and MAA on the trinitrophenyl-lipopolysaccharide (TNP-LPS) antibody plaque-forming cell (PFC) response, which we previously demonstrated to be a sensitive end point. Female inbred Lewis, Fischer 344 and Wistar/Furth, and outbred Sprague-Dawley rats were dosed by gavage with either ME or MAA at dosages of 0.33 to 2.64 mmol/kg/day for 10 consecutive days. Female inbred C3H and C57BL/6J, hybrid B6C3F1, and outbred CD-1 mice were similarly dosed with equimolar dosages of 0.66 to 5.28 mmol/kg/day ME or MAA. All animals were immunized on day 9 of dosing and PFC responses evaluated 3 days later. Suppression of the PFC response was observed in all strains of rats at 2.64 mmol/kg/day ME or MAA. Lewis and Wistar/Furth rats were found to be the most sensitive strains with suppression at levels as low as 0.66 mmol/kg/day ME or MAA. While ME and MAA dosing resulted in suppression of the TNP PFC response in all the rat strains tested, such treatment did not suppress this PFC response in any of the mouse strains examined. These results indicate that under the conditions of this study rats, but not mice, are immunosuppressed by ME and MAA exposure, and that the susceptibility to immunosuppression differs among rat strains.