Effects of delta9-tetrahydrocannabinol in Lewis lung adenocarcinoma cells in tissue culture.

We found a dose-related decrease in DNA synthesis in transformed cell cultures treated with delta9-tetrahydrocannabinol (delta9-THC). The decrease, observed over a 4-hour period, was not accompanied by a change in the radioactive precursor pool as compared to that of control culture. The distribution of labeled products clearly differed from that observed after treatment with cytosine arabinoside. delta9-THC inhibited DNA synthesis at some point beyond the uptake of 3H-thymidine.

Antineoplastic activity of cannabinoids.

Lewis lung adenocarcinoma growth was retarded by the oral administration of delta9-tetrahydrocannabinol (delta9-THC), delta8-tetrahydrocannabinol (delta8-THC), and cannabinol (CBN), but not cannabidiol (CBD). Animals treated for 10 consecutive days with delta9-THC, beginning the day after tumor implantation, demonstrated a dose-dependent action of retarded tumor growth. Mice treated for 20 consecutive days with delta8-THC and CBN had reduced primary tumor size. CBD showed no inhibitory effect on tumor growth at 14, 21, or 28 days. Delta9-THC, delta8-THC, and CBN increased the mean survival time (36% at 100 mg/kg, 25% at 200 mg/kg, and 27% at 50 mg/kg, respectively), whereas CBD did not. Delta9-THC administered orally daily until death in doses of 50, 100, or 200 mg/kg did not increase the life-spans of (C57BL/6 times DBA/2)F1 (BDF1) mice hosting the L1210 murine leukemia. However, delta9-THC administered daily for 10 days significantly inhibited Friend leukemia virus-induced splenomegaly by 71% at 200 mg/kg as compared to 90.2% for actinomycin D. Experiments with bone marrow and isolated Lewis lung cells incubated in vitro with delta9-THC and delta8-THC showed a dose-dependent (10(-4)-10(-7)) inhibition (80-20%, respectively) of tritiated thymidine and 14C-uridine uptake into these cells. CBD was active only in high concentrations (10(-4)).

Maleic vinyl ether activation of murine macrophages against lung-metastasizing tumors.

A 16,500 molecular weight fraction of maleic vinyl ether (MVE-2) induced tumoristatic and tumoricidal activity in peritoneal macrophages of BALB/c and C57BL/6 mice following i.p. administration. Growth of B16 melanoma cells in vitro was inhibited up to 85% by MVE-2-activated, but not resident, peritoneal macrophages. In a tritiated thymidine release assay, B16 melanoma cells, and to a lesser extent Madison 109 lung carcinoma cells, were also sensitive to the cytolytic action of MVE-2-activated peritoneal macrophages. Administration i.v. of MVE-2 resulted in tumoristatic and tumoricidal activity in alveolar macrophages against radiolabeled B16 and Madison 109 lung carcinoma target cells. MVE-2-activated alveolar macrophages significantly inhibited L5178Y lymphoma colony formation following a 48-hr macrophage-tumor cell coincubation. BALB/c mice bearing the lung-metastasizing Madison 109 lung carcinoma footpad tumor were given MVE-2 i.v., using the same dosing regimen that induced alveolar macrophages to be tumoricidal in vitro. Significant increases in life span were observed, suggesting that the antitumor activity of MVE-2 in this tumor system may be mediated by the activation of alveolar macrophages, with a resulting decrease in metastatic growth in the lung.

The inhibition of DNA synthesis by cannabinoids.

Several of the cannabinoids found in marihuana have been shown to inhibit tumor growth and increase the life-span of mice bearing the Lewis lung adenocarcinoma. When trypsin-dispersed isolated Lewis lung cells are incubated in vitro, they maintain their capacity to carry out macromolecular synthesis (RNA, DNA, protein). This process can be inhibited by cytosine arabinoside, actinomycin D, or methyl-1-(2-chloroethyl)-3-cyclohexyl-1-nitrosourea, whereas cyclophosphamide, an agent that must be bioactivated, was inactive. Inhibition of DNA synthesis as measured by [3H]thymidine uptake into acid-insoluble material was used as an index of cannabinoid activity against isolated Lewis lung cells, L1210 leukemia cells, and bone marrow cells incubated in vitro delta9-, delta8-, 1-hydroxy-3-n pentyl-, and 1-delta8-tetrahydrocannabinol, and cannabinol demonstrated a dose-dependent inhibition of DNA synthesis whereas cannabidiol and 1-hydroxy-3-n-pentylcannabidiol were markedly less inhibitory in our in vitro cell systems. Furthermore, our in vitro observations with these cannabinoids are supported by in vivo tumor inhibition studies. Ring modifications as in cannabichromene or cannabicyclol abolish in vitro activity as does dihydroxylation at the 8beta and 11 positions of 1-delta9-trans-tetrahydrocannabinol. Delta9-trans-tetrahydrocannabinol demonstrated the least toxicity of all inhibitory cannabinoids in vivo; this is supported by its lesser effect on bone marrow DNA synthesis in vitro.

Silicone-induced modulation of natural killer cell activity.

Current controversy regarding the effects of silicone gel mammary implants on the immune system has led to increased focus on the potential biological activity of silicone materials. Studies were undertaken in the B6C3F1 mouse to evaluate the immunotoxicological effects of the following components of a mammary gel prosthesis: polydimethylsiloxane fluid, silicone gel, elastomer shell and a polyurethane implant cover. Material was implanted subcutaneously (s.c.) for either 10 or 180 days. The only toxicological or immunological parameter which differed from control values was the natural killer (NK) cell activity in gel implanted mice. In these animals, basal NK activity was decreased. NK activity was comparably inhibited in female Fischer 344 rats implanted with silicone gel following short term (14 or 30 days) as well as chronic (1 year) exposure. The response was variable in both the rat and mouse. Host resistance to B16F10 melanoma in the mouse is known to be related to NK activity. Despite suppression of NK activity following gel implantation, host resistance was unaltered. Inhibition of NK activity by the administration of anti-asialo GM1 indicated that resistance was not adversely affected until NK activity was decreased by 40 to 50%. As with basal NK activity, augmented NK activity was inhibited in gel implanted rats when compared to controls. Administration of polyinosinic:polycytidylic acid to gel implanted rats resulted in an increase of approximately 65% in NK activity compared to gel implanted controls. This level of augmented NK activity was significantly less than the level of augmented NK activity in vehicle implanted animals where 100% enhancement in NK activity was noted. The results of these studies indicate that (1) NK cytolytic activity is altered in two animal models, the mouse and rat, although the results were variable, that (2) the level of suppression noted in the mouse is ineffective when compared to the level of suppression required to alter host resistance to B16F10 melanoma and that (3) the gel implanted animals exhibit a suppressed response to NK augmentation.

Suppression of the in vitro specific antibody response by 12-O-tetradecanoylphorbol-13-acetate (TPA) in the mouse.

The tumor promoter, 12-O-tetradecanoylphorbol-13-acetate (TPA), has several effects on the immune system. The effect of TPA on the in vitro antibody response to sheep red blood cells (sRBC) was studied. Spleen cells treated in vitro with TPA resulted in a dose-dependent inhibition of the IgM antibody forming cell (AFC) response with an IC50 of 0.74 nM. Nontumor promoting analogs at concentrations up to 1000 nM had no effect on this system. 2-Mercaptoethanol (2ME), which is known to augment macrophage function in this assay, did not reverse the inhibition. Spleen cells were separated into plastic adherent cells (ADC) and nonadherent cells (NAC). When NAC were treated with TPA and cultured with untreated ADC, the inhibition was seen. However, treating the ADC alone did not result in an inhibition. These results show that TPA will suppress the in vitro antibody response in the mouse and that the suppression is due to a selective effect on the plastic nonadherent cell population. The study of these effects of TPA may allow us to gain insight into the mechanism of its tumor promoting activity and to use it as a tool to study the modulation of the immune system.

Immunotoxic effects of diethylstilbestrol on host resistance: comparison with cyclophosphamide.

To evaluate the usefulness of host resistance assays for measurement of immunotoxicologic effects of chemicals, the immunosuppressive effects of exposure to diethylstilbestrol (DES) were compared with the effects of treatment with the known immunosuppressive drug cyclophosphamide (CPS). A panel of six host resistance models was evaluated, including infection with the bacterium Listeria monocytogenes, herpes simplex virus type 2 (HSV-2), and encephalomyocarditis virus (EMC), the yeast Cryptococcus neoformans, the parasite Naegleria fowleri, and transplantation of the B16F10 melanoma tumor. The results demonstrate a general correlation between the effects of CPS and DES on host resistance. Acute treatment with CPS (200 mg/kg) markedly depressed resistance to the microbial infections with L. monocytogenes and HSV, and exposure to DES usually also decreased resistance in a dose dependent manner. Moreover, CPS had no marked effect on resistance to N. fowleri and EMC virus, and exposure to DES also had a neglible or slight effect. There were, however, two model systems in which the effects of CPS and DES diverged. Whereas treatment with DES produced no significant effect on resistance to C. neoformans, acute treatment with CPS prior to the fungal infection produced a marked increase in resistance. Also, while treatment with CPS markedly increased B16F10 lung metastases, treatment with DES significantly decreased the incidence and number of lung metastases. The data support the general validity of host resistance assays, particularly with models of short disease course, for measuring immunosuppression. However, the results also emphasize the complexity of interpreting effects of environmental chemicals on host resistance, because of the interplay of such factors as relative times of exposure to the chemical in relation to pathogenesis of infection, the length of the disease course, the nature of the operative host defense mechanisms, and the compensatory recovery of these mechanisms.

In vitro immunotoxicological assays for detection of compounds requiring metabolic activation.

A system for metabolic activation of cyclophosphamide (CP), consisting of a crude microsomal fraction of mouse liver and necessary cofactors (S9 mix), was interfaced with three murine cell culture assays for immunotoxicity. These assays were: the Mishell-Dutton assay for in vitro antibody formation, splenic lymphocyte responsiveness to mitogens and bone marrow cell cultures. There was no effect of CP at doses up to 261 microgram/ml (lmM) on any of the parameters measured unless S9 mix was included. Much greater potency was achieved if the S9 mix was prepared from livers of mice pretreated with phenobarbital. Under these conditions and dose-related inhibition of plaque-forming cells (PFC) in the Mishell-Dutton assay was observed, yielding an ED50 of 6.3 microgram/ml. When splenic lymphocytes were exposed to CP in the presence of induced S9 mix, a dose related inhibition of the response to the B-cell mitogen, lipopolysaccharide (LPS), and to the T-cell mitogen, concanavalin A (Con A), was observed. For the optimum LPS concentration, the ED50 for CP was 8.1 microgram/ml; for the optimum concentration of Con A, the ED50 was 6.7 microgram/ml. DNA synthesis was not inhibited by the doses used. When bone marrow cells were exposed to CP in the presence of induced S9 mix, the stem cell population, enumerated by colonization in semisolid medium, was reduced in a dose-dependent manner, with an ED50 of 5.2 microgram/ml. Again, DNA synthesis was not affected unless higher doses of CP were used.

Toxicology of organic drinking water contaminants: trichloromethane, bromodichloromethane, dibromochloromethane and tribromomethane.

This study evaluated the subchronic toxicity of selected halomethanes which are drinking water contaminants. The compounds studied were trichloromethane, bromodichloromethane, dibromochloromethane and tribromomethane. Subchronic 14-day gavage studies were performed with the use of doses encompassing one-tenth the LD50 for the compounds. A 90-day gavage study of one of the compounds, trichloromethane, was also done. Parameters observed included body and organ weights, histopathology, hematology, clinical chemistries, and hepatic microsomal enzyme activities. Toxicity to the humoral immune system was assessed by measuring the number of splenic IgM antibody-forming cells and the serum antibody level to sheep erythrocytes. Cell-mediated immunity was evaluated by measuring the delayed type hypersensitivity response and popliteal lymph node proliferation response to sheep red blood cells. The functional activity of the reticuloendothelial system, as measured by the vascular clearance rate and tissue uptake of 51Cr sheep red blood cells was also determined. The major effects of the halomethanes were increased liver weights, elevations of SGPT and SGOT, decreased spleen weights and a decrease in the number of splenic IgM antibody-forming cells. The humoral immune system appeared to be an indicator of halomethane toxicity. There is evidence that subchronic 14-day exposure may be of greater value than long-term studies in determining the toxicity of these compounds.

Humoral and cell-mediated immune status in mice exposed to chloral hydrate.

Chloral hydrate has been found in our drinking water supplies at levels up to 5 micrograms/1. The purpose of this study was to evaluate the functional status of the immune system in random-bred CD-1 mice exposed to chloral hydrate for 14 and 90 days. Male mice, following 14 or 90 days of exposure to 1/10 and 1/100 the actual oral LD50, exhibited no alterations in either humoral or cell-mediated immunity. However, female mice exposed for 90 days to chloral hydrate in the drinking water demonstrated a significant depression in humoral immune function. This depression was observed when spleen cells from exposed mice were evaluated for their ability to produce antibody against sheep erythrocytes. These females did not demonstrate any changes in cell-mediated immune status.

In vivo assessment of immunotoxicity.

The organs, tissues, and cells of the lymphoreticular system have received considerable attention as targets for chemicals causing adverse effects. A basic toxicological approach is described for assessing the risk of a chemical perturbing the immune system. CD-1 mice were exposed for 14 or 90 days to one of several chlorinated hydrocarbons: 1,2-dichloroethane, 1,2-dichloroethylene or 1,1,2-trichloroethylene. Other mice were exposed to dexamethasone, a known immunosuppressive agent. The immune system is evaluated against a background of the more standard toxicological parameters such as fluid consumption, body and organ weights, hematology, clinical chemistries, and blood coagulation. Reported here are the results for the male mice after 14-day exposure to three chlorinated hydrocarbons and after 90-day exposure to 1,2-dichloroethane and dexamethasone.Acute toxicity studies were performed to provide a basis for doses used in the subchronic studies. The LD(50) values are reported. The status of the humoral immune system was determined by measuring the number of IgM spleen antibody-forming cells to sRBC, the serum antibody level to sRBC, and the lymphocyte response to the B-cell mitogen, LPS. Of the three chlorinated hydrocarbons, only dichloroethane produced a significant (p < 0.05) reduction in antibody-forming cells. The other two chemicals produced trends towards suppression. Mice exposed to dichloroethane in the drinking water for 90 days showed no alteration in AFC, serum antibody titers or response to the B-lymphocyte mitogen, LPS. Subchronic 90-day exposure to dexamethasone produced a dose-dependent inhibition of AFC/spleen but not AFC/10(6) spleen cells when measured on the peak day of response. Response to LPS was not altered, and spleen weight and spleen cell number were reduced as much as 42%. These data suggest that dexamethasone administered in the drinking water is nonspecifically cytotoxic to the spleen cells.Cell-mediated immunity was assessed by measuring the DTH response to sRBC and the response to the T-lymphocyte mitogen, concanavalin A. After 14 days of exposure, trichloroethylene produced a 15 and 60% suppression at 24 and 240 mg/kg, respectively. Dichloroethylene produced a non-dose-dependent inhibition at 4.9 and 49 mg/kg, which was slight, but significant (p < 0.05). Subchronic 90-day exposure to dichloroethane did not alter the DTH response or spleen lymphocyte response to concanavalin A. In contrast, dexamethasone produced a dose-dependent inhibition of the DTH response and a hyperresponsiveness to concanavalin A.Dichloroethane did not alter the functional activity of the reticuloendothelial system, as measured by the vascular clearance rate and tissue uptake of (51)Cr sRBC. In the case of dexamethasone exposure, only the spleen and thymus showed decreased uptake of (51)Cr sRBC, which was directly related to decrease in size. The approaches and results from these types of studies provide a basis for judging a chemical's potential risk to the immune system.

Toxicology of chloral hydrate in the mouse.

Chloral hydrate has been found in our drinking water supplies at levels up to 5 micrograms/1. The purpose of this study was to evalute the acute and subchronic toxicology of chloral hydrate in the random-bred CD-1 mouse, to provide data for risk assessment. The acute oral LD50 of this compound was 1442 and 1265 mg/kg in male and female mice, respectively. Acute toxicity appeared to be related to depression of the central nervous system. Fourteen-day exposure by gavage in male mice at doses 1/10 and 1/100 the LD50 caused an increase in liver weight and a decrease in spleen weight at the highest dose level. Based on the data derived from 14 days of exposure, a 90-day study was performed. The compound was delivered via the drinking water; levels of the compound delivered per day were equivalent to those dosed in the 14-day study. The target organ in both sexes appeared to be the liver, with the males most affected. Male mice demonstrated a dose-related hepatomegaly accompanied by significant changes in serum chemistries and hepatic microsomal parameters. The females did not demonstrate the hepatomegaly observed in males, but did show alterations in hepatic microsomal parameters. No other significant toxicological changes were observed in either sex following 90 days of exposure.

Respiratory exposure to diesel exhaust particles decreases the spleen IgM response to a T cell-dependent antigen in female B6C3F1 mice.

We investigated the systemic immunotoxic potential of respiratory exposure to diesel exhaust particles (DEP) in this study. Female B6C3F1 mice (approximately 8 weeks old) were exposed to increasing concentrations of DEP intratracheally, 3 times every two weeks, and sacrificed 2 or 4 weeks after the first exposure. The systemic toxicity and immune status in mice were evaluated. Mice exposed to DEP (1 to 15 mg/kg) showed no significant changes in body, spleen, or liver weights. Lung weights were increased in the mice exposed to 15 mg/kg DEP for 2 or 4 weeks. Except for a decreased platelet count, no significant alterations occurred in hematological parameters following DEP exposure. The number of splenic anti-sheep red blood cell (sRBC) IgM antibody-forming cells (AFC) decreased following DEP exposure for 2 weeks. This effect was less severe following 4 weeks of exposure and was only evident in the high dose group. Exposure to DEP also resulted in a significant decrease in the absolute numbers and the percentages of total spleen cells for total, CD4(+), and CD8(+) T cells, while the numbers of B cells and total nucleated cells in spleen were not significantly changed. The proliferative response of splenocytes to the T-cell mitogen, concanavalin A (ConA), as well as their production of IL-2 and IFN-gamma, was decreased dose-dependently following exposure of mice to DEP for 2 weeks, whereas proliferation was not changed in response to anti-CD3 monoclonal antibody. In summary, short-term respiratory exposure of mice to DEP resulted in systemic immunosuppression with evidence of T cell-mediated and possibly macrophage-mediated mechanisms.

Immunological responses of mice following administration of natural rubber latex proteins by different routes of exposure.

Although the prevalence of IgE-mediated latex allergy has increased over the past decade, the circumstances which culminate in sensitization remain uncertain. The objective of these studies was to evaluate the role which sensitization route plays in the development of latex allergy using murine models representative of potential exposure routes by which health care workers (topical and respiratory) and spina bifida patients (subcutaneous) may be sensitized. BALB/c mice administered latex proteins by the subcutaneous, topical, intranasal, or intratracheal routes exhibited dose-responsive elevations in total IgE. In vitro splenocyte stimulation initially demonstrated specificity of the murine immune response to latex proteins. Subsequently, immunoblot analysis was used to compare latex-specific IgE production amongst sensitization routes. Immunoblots of IgE from subcutaneously sensitized mice demonstrated recognition of latex proteins with molecular weights near 14 kDa and 27 kDa. These protein sizes are consistent with the molecular weights of major latex allergens (Hev b 1 and Hev b 3), to which high percentages of spina bifida patients develop antibodies. Mice sensitized by intratracheal or topical administration exhibited combined IgE recognition of latex proteins near 14 kDa, 35 kDa, and 92 kDa. These molecular weights are similar to other latex allergens (Hev b 6, Hev b 2, and Hev b 4) commonly recognized by IgE of health care workers. Mice sensitized to latex proteins by topical, intranasal, or intratracheal exposures exhibited bronchoconstriction as evaluated by whole body plethysmography following respiratory challenge with latex proteins. Subcutaneously sensitized mice were unresponsive. These differences in latex-specific IgE immunoblot profiles and altered pulmonary function amongst the four different sensitization routes suggest that exposure routes leading to sensitization may play a role in determining the primary allergen(s), and the clinical manifestation of the allergic responses.

Analysis of gene expression induced by irritant and sensitizing chemicals using oligonucleotide arrays.

Chemical-induced allergy continues to be an important occupational health problem. Despite decades of investigation, the molecular mechanisms underlying chemical-induced hypersensitivity and irritancy remain unclear because of the complex interplay between properties of different chemicals and the immune system. In this study, gene expression induced by toluene diisocyanate (TDI, a primarily IgE-inducing sensitizer), oxazolone (OXA, a cell-mediated hypersensitivity inducing sensitizer), or nonanoic acid (NA, a non-sensitizing irritant) was investigated using gene arrays. Female BALB/c mice were dermally exposed on the ears once daily for 4 consecutive days. On day 5, the lymph nodes draining the exposure sites were collected and used for RNA extraction and subsequent hybridization to Affymetrix Mu6500 oligonucleotide arrays. Of the 6519 genes on the arrays, there were 44, 13, and 51 genes in the TDI-, OXA-, and NA-exposed samples, respectively, that displayed a minimum of twofold change in expression level relative to the vehicle control. There were 32, 19, and 19 genes that were differentially expressed (with a minimum of twofold change) between TDI and OXA, TDI and NA, OXA and NA, respectively. The differentially expressed genes include immune response-related genes, transcriptional factors, signal transducing molecules, and Expressed Sequence Tags. Based on the gene array results, candidate genes were further evaluated using RT-PCR. There was only about 47% concordance between the gene array and RT-PCR results.

Comparison of mouse strains using the local lymph node assay.

The local lymph node assay (LLNA), as recommended by the Interagency Coordinating Committee on the Validation of Alternative Methods (ICCVAM), only allows for the use of CBA mice. The objective of these studies was to begin to assess the response of chemical sensitizers in the LLNA across six strains of female mice (C57BL/6, SJL/J, BALB/c, B6C3F1, DBA/2 and CBA). The moderate sensitizer alpha-hexylcinnamaldehyde (HCA) was chosen as the test chemical, while toluene diisocyanate (TDI) and 2,4-dinitrofluorobenzene (DNFB) were evaluated at single concentrations as positive controls. Draining lymph node cell proliferation following acetone exposure varied across strains. SJL mice had a significantly higher degree of proliferation with 2111 d.p.m./2 nodes. The remaining five strains demonstrated responses which ranged from 345 to 887 dpm/2 nodes. DBA/2, B6C3F1, BALB/c and CBA mice had essentially equal levels of lymph node proliferation following exposure to the three chemicals. While C57BL/6 mice gave similar results as CBA mice following DNFB and HCA administration, the LLNA response to TDI was considerably lower. SJL mice provided low stimulation indexes (SI) values for all three chemicals evaluated. Regardless of the level of LLNA response, all six mouse strains identified the sensitization potential of HCA, TDI or DNFB. Based on these studies, DBA/2, B6C3F1 and BALB/c mice are good choices for continued evaluation as additional mouse strains for use in the LLNA.

Carbon tetrachloride is immunosuppressive and decreases host resistance to Listeria monocytogenes and Streptococcus pneumoniae in female B6C3F1 mice.

Carbon tetrachloride (CCl(4)) is an environmental contaminant that has been detected in ambient air, seawater, surface-water and snow. The immunotoxic potential of CCl(4) was evaluated in female B6C3F1 mice. The animals were administered with CCl(4) daily for 14 days at doses of 50, 100, 500 or 1000 mg/kg body weight by gavage with corn oil as a vehicle. Exposure to CCl(4) resulted in an increase of liver weight but not the body weight and the weights of brain, spleen, lungs, thymus and kidneys. Exposure to CCl(4) produced minimal effect on differential hematological parameters; however, it produced a significant increase in serum glutamic-pyruvic transaminase (SGPT) levels in all dose groups while other serum chemistries showed sporadic increases, primarily at the dose level of 1000 mg/kg. Exposure to CCl(4) produced a decreased humoral immune response; the IgM antibody forming cell (AFC) response to sheep red blood cells (sRBC) was suppressed with the maximal decrease (45%) observed at the dose level of 1000 mg/kg. The IgM serum titer to sRBC was also reduced with a maximal decrease (54%) observed at the dose level of 500 mg/kg. Although exposure to CCl(4) had no effects on the mixed leukocyte response (MLR), cytotoxic T lymphocyte activity and natural killer (NK) cell activity, a decrease in both the absolute number and the percentage of CD4(+)CD8(-) at the dose level of 500 mg/kg was observed. The functional activity of the mononuclear phagocyte system was compromised as reflected by a decrease in the vascular clearance of (51)Cr-sRBC and a decrease in the uptake of (51)Cr-sRBC by the liver. Finally, in the two host resistance models evaluated, exposure to CCl(4) decreased host resistance to both Streptococcus pneumoniae and Listeria monocytogenes with greater susceptibility to the latter. Overall, these studies demonstrate that CCl(4) was immunosuppressive in female B6C3F1 mice.

Immunotoxicologic studies with CI-959, a novel benzothiophene cell activation inhibitor.

CI-959 is an orally effective inhibitor of cellular activation in both in vitro and animal models. To assess the effects of CI-959 on immune function, male Fischer 344 rats were evaluated for splenic T- and B-lymphocyte populations, antibody-forming cell response to sheep red blood cells (sRBC), concanavalin A and pokeweed mitogen-induced lymphocyte proliferation, Natural Killer cell activity, and reticuloendothelial system clearance of sRBC. Host resistance was measured in female B6C3F1 mice using Listeria monocytogenes, Streptococcus pneumonia, and B16F10 melanoma models. CI-959 was administered to both species of rodents at 25, 50, and 75 mg/kg/day for 14 days. A vehicle control and two positive controls (cyclophosphamide and dexamethasone) were run concurrently. CI-959 generally did not suppress immunological responses in rats at doses lower than those which also altered body weight gain and reduced spleen and thymus weights. Natural Killer cell activity was significantly reduced at 50 and 75 mg/kg CI-959. At 75 mg/kg rats also exhibited a reduction in ability to make anti-sRBC antibody. The number of T- and B-lymphocytes, proliferative response to mitogens, and macrophage activity of the reticuloendothelial system were not affected by CI-959. CI-959 also did not alter resistance of mice to Listeria monocytogenes, Streptococcus pneumoniae, or B16F10 melanoma cells. Based on these ex vivo and in vivo assays, the rodent immune system does not appear to be a sensitive or toxicologically important target for CI-959.

Pharmacological activity and toxicity of phencyclidine (PCP) and phenylcyclohexene (PC), a pyrolysis product.

Initial acute behavioral studies in mice indicated that phencyclidine (PCP) produced marked motor impairment as measured by the inverted screen technique with an ED50 value of 4.1 muMole/kg (i.v.). Phenylcyclohexene (PC) was considerably less active with an ED50 value of 325 muMole/kg (i.v.). PCP was also shown to be more lethal than PC as acute (24 hr; i.v. injection) LD50 values (muMoles/kg) in males were 57 and 448, and in females were /6 and 425, respectively. A greater acute lethality was also produced by PCP after i.p. and p.o. administration. Subchronic (14-day) exposure (i.p.) to PCP at doses up to approximately 40 percent of the acute LD50 value (123.6 muMole/kg, i.p., daily) was without significant effect on body and organ weights, hematology and clinical chemistry, and humoral and cell-mediated immunity. Higher doses of PCP were not possible because of acute lethality. Subchronic exposure to PC (63.4, 317, and 634.5 muMoles/kg; 4 percent, 20 percent and 40 percent of acute i.p. LD50 value, respectively) produced several marked effects. At the highest dose tested, body weight and thymus weight in both males and females, and liver weight in males were significantly decreased. The spleen weight of males exposed to 317 muMole/kg PC was also significantly decreased. Humoral immunity (production of antibody forming cells) was significantly inhibited in both males and females exposed to PC. In contrast, cell-mediated immunity (development of a delayed-type hypersensitivity response) was only significantly inhibited in females. As PCP has no measurable toxicity under these conditions and PC produced significant effects at relatively high doses, the results suggest that neither chemical is exceptionally toxic following subchronic exposure.

Qualitative and quantitative experimental models to aid in risk assessment for immunotoxicology.

We have previously reported on the design and content of a screening battery using a "tier" approach for detecting potential immunosuppressive compounds in mice [1]. This battery was composed of various immune function, immunopathology and host resistance tests, the results of which could help establish the potential of chemical and biological agents to cause immunosuppression. The data from these studies, which now encompass over 50 compounds, have been analyzed in an attempt to improve future testing strategies and provide information to aid in the risk assessment process. Specifically, the following two issues will be addressed; what are the likelihood(s) for each of the individual tests and testing configurations to accurately identify immunotoxic compounds? and what are the quantitative and qualitative relationships between the immune tests and host resistance assays?