Mode of action and dose-response framework analysis for receptor-mediated toxicity: The aryl hydrocarbon receptor as a case study.

Dioxins and dioxin-like compounds are tumor promoters that cause liver cancer in rats and mice. The aryl hydrocarbon receptor (AHR) has been implicated as a key component in this tumor promotion response. Despite extensive knowledge of the toxicology of dioxins, no mode of action (MOA) hypothesis for their tumorigenicity has been formally documented using the Human Relevance MOA framework developed by the International Programme on Chemical Safety (IPCS). To address this information gap, an expert panel was convened as part of a workshop on receptor-mediated liver tumorigenicity. Liver tumors induced by ligands of the AHR were assessed using data for dioxins and related chemicals as a case study. The panel proposed a MOA beginning with sustained AHR activation, eventually leading to liver tumors via a number of other processes, including increased cell proliferation of previously initiated altered hepatic foci, inhibition of intrafocal apoptosis and proliferation of oval cells. These processes have been identified and grouped as three key events within the hepatocarcinogenic MOA: (1) sustained AHR activation, (2) alterations in cellular growth and homeostasis and (3) pre-neoplastic tissue changes. These key events were identified through application of the Bradford-Hill considerations in terms of both their necessity for the apical event/adverse outcome and their human relevance. The panel identified data supporting the identification and dose-response behavior of key events, alteration of the dose-response by numerous modulating factors and data gaps that potentially impact the MOA. The current effort of applying the systematic frameworks for identifying key events and assessing human relevance to the AHR activation in the tumorigenicity of dioxins and related chemicals is novel at this time. The results should help direct future regulatory efforts and research activities aimed at better understanding the potential human cancer risks associated with dioxin exposure.

Evaluating the impact of exposure to environmental contaminants on human health.

Humans are exposed daily to low concentrations of many different chemical substances, natural and some man-made. Although many of these substances can be toxic at high levels, typical exposures are far below the effect levels. The responses produced by man-made aromatic hydrocarbon receptor agonists, such as dioxins, polychlorinated dibenzofurans, coplanar polychlorinated biphenyls, and polycyclic aromatic hydrocarbons, are also produced, often to greater extents [corrected], by naturally occurring constituents of fried meat, cabbage, broccoli, cauliflower, cocoa, and curry. Our society seems to be concerned about the health risks associated only with the synthetic chemicals, regardless of their proportional contribution to the total agonist activity, and regulates on the basis of such concerns. It would be more protective of the public health to determine acceptable concentrations for each type of response, regardless of the origin of the inducing agent, and issue advisories or regulations accordingly.

Immunosuppressive potential of several polycyclic aromatic hydrocarbons (PAHs) found at a Superfund site: new model used to evaluate additive interactions between benzo[a]pyrene and TCDD.

Exposure to environmental pollution is rarely limited to a single compound or even a single class of compounds. The Superfund site located in Massena, NY, is contaminated by both halogenated aromatic hydrocarbons (HAHs) and polycyclic aromatic hydrocarbons (PAHs). Since representatives of both HAHs and PAHs are capable of binding to the aromatic hydrocarbon receptor (AhR), two well-documented AhR-mediated effects, immunosuppression and induction of hepatic aryl hydrocarbon hydroxylase (AHH) activity, were used to evaluate the individual and interactive toxicity of these compounds. Fifteen PAHs were first screened for their ability to suppress the antibody response in C57BL/6 (Ah+/+) mice immunized 12 h after a single oral dose of 0.1, 1, 10, or 100 mg/kg. Acenaphthene, anthracene, benzo[g,h,i]perylene, fluoranthene, fluorene, naphthalene, phenanthrene, and pyrene had little or no effect. Seven PAHs caused > 50% suppression at 100 mg/kg. Listed in order of decreasing potency they were benzo[k]fluoranthene, benzo[b]fluoranthene, indeno[1,2,3,c,d]pyrene, benzo[a]pyrene, chrysene, dibenzo[a,h]anthracene, and benz[a]anthracene. Chrysene and benzo[a]pyrene (B[a]P), were further evaluated to determine the dependence of these effects on the Ah phenotype by comparing responses of C57BL/6 and congenic B6.D2 (Ah-/-) mouse strains. Chrysene immunosuppression was maximal at 0.1 mg/kg and was Ah phenotype-independent whereas chrysene AHH induction was Ah phenotype-dependent, but a 100-fold less sensitive indicator of exposure. In contrast, B[a]P immunosuppression and AHH induction were coincident in B6 mice and Ah phenotype-dependent. In the final phase, a new approach was used to evaluate toxic interactions. This approach considers the mechanism of action of each compound and accounts for the fact that the extent of increase in toxic response caused by an incremental change of dose is determined by its position on the dose-response curve rather than on the absolute amount of dose administered. Thus, the immunotoxic effects of combined exposure to B[a]P and the AhR ligand, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), a representative HAH, were evaluated by combining the ED20 of B[a]P with the difference between the ED20 and ED40 of TCDD, and vice versa, to produce 40% suppression. The results of the combination were consistent with additivity regardless of the composite arrangement or phenotype although some antagonism could not be excluded with certainty.

2,3,7,8-Tetrachlorodibenzo-p-dioxin inhibits differentiation of normal diploid rat osteoblasts in vitro.

The influence of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), a potent halogenated aromatic hydrocarbon, on the development of bone tissue-like organization in primary cultures of normal diploid calvarial-derived rat osteoblasts was examined. Initially, when placed in culture, these cells actively proliferate while expressing genes associated with biosynthesis of the bone extracellular matrix. Then, post-proliferatively, genes are expressed that render the osteoblast competent for extracellular matrix mineralization and maintenance of structural as well as functional properties of the mature bone-cell phenotype. Our results indicate that, in the presence of TCDD, proliferation of osteoblasts was not inhibited but post-confluent formation of multicellular nodules that develop bone tissue-like organization was dramatically suppressed. Consistent with TCDD-mediated abrogation of bone nodule formation, expression of alkaline phosphatase and osteocalcin was not upregulated post-proliferatively. These findings are discussed within the context of TCDD effects on estrogens and vitamin D-responsive developmental gene expression during osteoblast differentiation and, from a broader biological perspective, on steroid hormone control of differentiation.

Potentiation and antagonism of 2,3,7,8-tetrachlorodibenzo-p-dioxin effects in a complex environmental mixture.

There is increasing need to understand the toxicity of complex environmental mixtures. The organic phase of a leachate (OPL) from the Love Canal chemical dump site is a complex mixture that contains over 100 organic compounds, including 0.74 ppm 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Mice congenic at the Ah locus were used to evaluate several toxic effects of the OPL, including immune function and hepatic enzyme induction. OPL toxicity was compared with that of pure TCDD in both C57BL/6J Ahb/b and congenic C57BL/6 Ahd/d (B6.D2) mice. Mice were given single oral doses of up to 2 g OPL/kg or 100 micrograms TCDD/kg, immunized, and evaluated after 7 days. The TCDD equivalent of the OPL was determined to be 3.9 and 5.0 ppm in C57BL/6J and B6.D2 mice, respectively. This is six times the TCDD content. The Ah phenotype-dependent response ratio was calculated by dividing the dose required to cause an effect in the B6.D2 strain by the dose causing the same effect in the C57BL/6J strain. Ratios based on both ED50s and the lowest observed adverse effect levels were used to determine whether each adverse effect was Ah phenotype-dependent, the extent to which TCDD contributed to the effect, whether there were interactive effects between the AhR ligands and nonligands and if they were additive, antagonistic, or synergistic, and whether the response was predictable based on the known chemical composition of the mixture. It was concluded that the non-TCDD component potentiated TCDD immune suppression, and possibly thymic atrophy, through AhR mechanisms. In contrast, this analysis indicated that the non-TCDD component of the OPL antagonized the ability of the TCDD component to induce hepatic AHH activity whereas OPL hepatomegaly was caused primarily by the non-TCDD component of the OPL. This study demonstrates that the toxicity of mixtures containing TCDD may not be accurately predicted based on the TCDD content alone and that this approach could be useful in the toxicologic assessment and management of environmental contamination.

Rat small intestinal cytochromes P450 probed by warfarin metabolism.

Small intestinal cytochromes P450 (P450s) provide potential first-pass metabolism of ingested xenobiotics. To investigate this system, this study addresses the procedure for elution of enterocytes from male rat small intestine, histological evaluation of the elution procedure, and assessment of the functional microsomal P450s in small intestine of untreated and induced rats, using warfarin metabolism as a probe. Histologically it was demonstrated that villous enterocytes are initially detached in sheets and are subsequently eluted without clear resolution into villous tip, midvillous, and lower villous cells, contrary to previous reports. Crypt cells are eluted after cells from the villus. The following functional P450s were identified, using stereo- and regioselectivity of warfarin metabolism, in small intestinal microsomes: P4502B1 in untreated rats, P4501A1 in beta-naphthoflavone-induced rats, P4502B1 in phenobarbital-induced rats, and P4503A1/2 in pregnenolone-16 alpha-carbonitrile-induced rats. In contrast to hepatic microsomes from untreated or induced rats, P4502C11 and -2C6 were not present or inducible by these inducing agents in rat intestine. Western immunoblots, warfarin assays, and P450 assays all indicated that beta-naphthoflavone induced P4501A1 in small intestinal villous and crypt cells, but in contrast to the liver neither apo-P4501A2 nor functional P4501A2 was induced.

Application of clinical laboratory measurements to issues of environmental health.

Monitoring of biochemical constituents in serum is an important component in revealing potential toxicity in humans and experimental animals due to exposure to a variety of xenobiotic agents. The relative toxicity of pure compounds, usually at large doses, has helped elucidate the mode of action of these compounds and their relative risk. However, most actual cases of environmental exposure present an extensive range of components and the potential for synergistic or inhibitory interactions. In this paper we review two such environmental cases: The Love Canal chemical dump site in Niagara Falls, NY, and the transformer fire at the State Office Building in Binghamton, NY. We focus on the clinical laboratory measurements obtained in these studies (including serum glucose, triglycerides, aspartate aminotransferase, alanine aminotransferase, alkaline phosphatase, gamma-glutamyltransferase, lactate dehydrogenase, sodium and potassium), their usefulness, limitations, and application to such cases. Significant alterations in serum triglyceride and alanine aminotransferase levels were found in guinea pigs due to exposure to dioxins. These two tests were useful in estimating the 'equivalent' concentration of 2,3,7,8-tetrachlorodibenzo-p-dioxin in complex chemical mixtures.

Severity of disease induced by a pancreatropic Coxsackie B4 virus correlates with the H-2Kq locus of the major histocompatibility complex.

Coxsackie B viruses are known etiological agents of pancreatic diseases, including diabetes. The pathogenesis of these infections is influenced by both host and viral factors. In this report, we examined whether the outcome of Coxsackie B4 virus infection is dependent on the genes within the major histocompatibility complex (MHC). We generated a pancreatic variant, CB4-V and established an animal model system of pancreatitis with concurrent hypoglycemia in mice. Infection of various B10 H-2 congenic strains of mice revealed that the development of hypoglycemia with accompanying pancreatitis was independent of the MHC haplotype. However, the severity of the disease as monitored by the extent and duration of hypoglycemia and by mortality rate was found to be associated with the H-2 haplotype, specifically the H-2Kq locus. Pancreatic damage induced by CB4-V appeared to be both immune-mediated and viral-mediated. Histological examination of pancreatic tissue from infected B10 H-2 congenic mice revealed an association between acute destruction of the exocrine pancreas and lymphocytic infiltration. This infiltration may correlate with immune-mediated destruction of the infected pancreatic tissue. Since preferential replication of CB4-V was not observed in the most susceptible B10 mouse strain, direct viral destruction may not be the major mechanism of pancreatic injury.

Teratology of 2,3,7,8-tetrachlorodibenzo-p-dioxin in a complex environmental mixture from the love canal.

The organic phase of a leachate (OPL) from the Love Canal chemical dump site contains more than 100 organic compounds including 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD). The teratogenic potential of OPL was determined in two inbred and one hybrid mouse strain which differ in their sensitivity to aromatic hydrocarbon (Ah) receptor-mediated toxicity. OPL was orally administered in corn oil on Days 6-15 of gestation to C57BL/6J mice (Ahb/Ahb) at doses of 0, 0.1, 0.3, 0.5, and 0.7 g kg-1 day-1 and to DBA/2J (Ahd/Ahd) females, which were mated with either DBA/2J or C57BL/6J males, at 0, 0.5, 1, and 2.0 g kg-1 day-1. In C57BL/6J mice, which express a high-affinity Ah receptor that avidly binds TCDD, the ED50's of OPL for cleft palate and hydronephrosis were 0.44 and 0.11 g OPL kg-1 day-1, respectively. Maternal mortality was 5% at the highest dose. In DBA/2J fetuses, which express a low-affinity receptor, neither treatment-related cleft palate nor hydronephrosis was induced by dose levels that caused 36% maternal mortality. In hybrid D2B6F1 fetuses, the incidence of cleft palate reached only 8% at 2 g OPL kg-1 day-1 but the ED50 for hydronephrosis was 0.76 g OPL kg-1 day-1. TCDD was similarly administered to pregnant C57BL/6J mice at 0, 0.5, 1, 2, and 4 micrograms kg-1 day-1 and to DBA/2J mice at 0, 0.5, 2, 4, and 8 micrograms kg-1 day-1. In C57BL/6J fetuses, the ED50's for cleft palate and hydronephrosis were 4.6 and 0.73 microgram TCDD kg-1 day-1, respectively. In DBA/2J fetuses the ED50's for cleft palate and hydronephrosis were 15.0 and 6.4 micrograms TCDD kg-1 day-1, respectively. Both the OPL and TCDD caused maternal hepatomegaly and thymic atrophy in all strains, but increased only C57BL/6J fetal weights. OPL decreased the number of fetuses per C57BL/6J dam at the two highest doses but there were no other reproductive effects in any of the groups. It was concluded that the OPL is teratogenic and that hydronephrosis is a sensitive measure of TCDD toxicity in a complex organic mixture. Based on the ED50's of OPL- and TCDD-induced cleft palate and hydronephrosis in the C57BL/6J strain, the OPL had TCDD equivalence of 6.6 and 10.5 ppm, respectively. These values compare closely with the chemical analysis of 3 ppm.(ABSTRACT TRUNCATED AT 400 WORDS)

Immunotoxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin in a complex environmental mixture from the Love Canal.

The organic phase of the leachate (OPL) from the Love Canal chemical dump site contains more than 100 organic compounds including 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). The immunotoxic potential of OPL was determined in two mouse strains which differ in their sensitivity to aromatic hydrocarbon (Ah) receptor-mediated toxicity. OPL was administered in corn oil in a single oral gavage to male BALB/cByJ (Ahb/Ahb) mice (0.5, 0.8, or 1.1 g/kg) and DBA/2J (Ahd/Ahd) mice (0.6, 0.9, or 1.3 g/kg). TCDD was similarly administered at 0.25, 1.0, 4.0, or 16.0 micrograms/kg. Two days later all mice were immunized with sheep erythrocytes (SRBC). The antibody response (PFC) and organ weights were evaluated 4 days later. OPL produced thymic atrophy and hepatomegaly in both strains at all dose levels. The PFC/spleen in BALB/cByJ mice was significantly reduced at the three doses to 34, 13, and 15%, respectively, of the control response. Serum anti-SRBC antibody levels and relative spleen weights were also reduced. The only immune effect in the DBA/2J mice was a decrease of the PFC/spleen to 58% of the control at the highest dose. TCDD decreased the relative thymus and spleen weights only in BALB/cByJ mice. However, TCDD produced hepatomegaly, a decrease in serum antibody, and a decrease in PFC/spleen in both BALB/cByJ and DBA/2J mice to 3 and 15%, respectively, at 16 micrograms/kg. Thus, the TCDD dose required to cause a 50% suppression (ED50) of PFC/spleen for the BALB/cByJ and DBA/2J strains was 1.84 and 3.89 micrograms/kg, respectively. The ED50 for OPL was 0.24 g/kg in BALB/cByJ mice. The TCDD concentration in the OPL was estimated to be 7.6 ppm, which agrees closely with the chemical analysis (3 ppm). The results suggest that the immunosuppression caused by OPL in BALB/cByJ mice was primarily due to TCDD, that the non-TCDD components of OPL diminished the TCDD immunotoxicity in the DBA/2J strain, and that the thymic atrophy and hepatomegaly were caused primarily by the non-TCDD components of the OPL.

Ah receptor mediated suppression of the antibody response in mice is primarily dependent on the Ah phenotype of lymphoid tissue.

Halogenated aromatic hydrocarbons act through the aromatic hydrocarbon (Ah) receptor in mice to produce a series of toxic effects of the immune system. The receptor protein is a product of the Ah gene locus. Ah responsive (Ahb/Ahb) mice express a high affinity receptor in both lymphoid and nonlymphoid tissues whereas nonresponsive Ahd/Ahd mice express a poor affinity receptor. To determine the role of the Ah receptor of lymphoid tissue relative to that of nonlymphoid tissue in the induction of immune impairment, bone marrow was used to reconstitute lethally irradiated mice of the same or opposite Ah phenotype. All mice were given 3,3',4,4'-tetrachlorobiphenyl (35 and 350 mumol/kg) ip 2 days before immunization with sheep erythrocytes (SRBC). The immune response to this T dependent antigen and organ weights were determined 5 or 7 days later in normal or chimeric mice, respectively. Monoclonal Lyt 1.1 and Lyt 1.2 antibodies were used to establish the origin of the cells which repopulated the chimeric thymuses. The immune responses of both BALB/cBy (Ahb/Ahb) and the BALB/cBy X DBA/2 hybrid, CByD2F1 (Ahb/Ahd), were significantly suppressed but DBA/2 mice were unaffected. The immune responses of chimeric BALB/cBy----BALB/cBy and BALB/cBy----DBA/2 (donor----recipient) mice were also significantly suppressed and thymic atrophy was observed in both cases. The serum anti-SRBC antibody titers of DBA/2----BALB/cBy chimeras were also significantly decreased although not to the same extent as in BALB/cBy----DBA/2 mice. Chimeric DBA/2----DBA/2 mice were not affected. These results indicate that the sensitivity to Ah receptor mediated suppression of the antibody response is primarily determined by the Ah phenotype of the lymphoid tissue.

Calculation of 2,3,7,8-TCDD equivalent concentrations of complex environmental contaminant mixtures.

Sufficient toxicological data are now available to permit use of conventional risk assessment techniques to estimate the hazards associated with human exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD). However, many real-world exposures involve complex mixtures of dibenzodioxins, dibenzofurans, and related compounds. Historical approaches to risk assessment on such mixtures have ranged from ignoring all compounds except 2,3,7,8-TCDD itself to assuming that all compounds have potencies equal to 2,3,7,8-TCDD. An alternative approach which uses existing literature data and analytical results to calculate the "2,3,7,8-TCDD equivalent" concentration of a mixture in order to "predict" its biological potency relative to 2,3,7,8-TCDD itself is advanced here. Previously reported in vivo acute and subchronic studies and some recently obtained analytical chemistry data are integrated here to clarify the utility of this important approach and to assess the uncertainties associated with its use. This predictive approach, and various conceptually similar ones, have now found wide applicability to the risk assessment process associated with exposure to complex mixtures of dioxins, dibenzofurans, and related compounds.

The effects of Love Canal soil extracts on maternal health and fetal development in rats.

The effects of a solvent extract of the surface soil of the Love Canal chemical dump site, Niagara Falls, New York, and of a natural extract, or leachate, which is drained from the canal for treatment, on the maternal health and fetal development were determined in rats. The solvent extract, which was contaminated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (2, 3,7,8-TCDD) at 170 ppb and numerous other chlorinated organic compounds with the primary identified components being the isomers of benzenehexachloride (BHC), was dissolved in corn oil and administered by gavage to pregnant rats at 0,25,75, or 150 mg crude extract/kg/day on Days 6-15 of gestation. A 67% mortality was observed at the highest dose. The rats were sacrificed on Day 20. Dose-related increases in relative liver weight accompanied by hepatocyte hypertrophy were observed at all dose levels. Fetal birthweight was decreased at 75 and 150 mg extract/kg/day. No major treatment-related soft tissue or skeletal malformations, except for delayed ossification, were observed. Based on literature values for BHC, all of the observed toxicity could be accounted for by the BHC contaminants of the extract. The crude organic phase of the leachate was administered to pregnant rats at 0,10,100, or 250 mg/kg/day as described above. Maternal weight gain decreased at 100 and 250 mg/kg/day, accompanied by 5 and 14% maternal mortality, and 1 and 3 dead fetuses, respectively. Early resorptions and the percentage of dead implants increased whereas fetal birthweights were decreased at 250 mg/kg/day. No major treatment-related soft tissue or skeletal malformations, except for delayed ossification, were observed. The primary components of the complex leachate by mass were tetrachloroethanes; however, 2,3,7,8-TCDD, which was present at 3 ppm, probably accounted for all the observed toxicity.

Mechanism of toxicity of 2,2,2-trifluoroethanol in rats.

2,2,2-Trifluoroethanol (TFE) is the toxic metabolite of the anesthetic agent fluroxene. TFE treatment (0.21 g/kg, ip) of male Wistar rats significantly reduced peripheral white blood cell count, bone marrow nucleated cellularity, and dry weight of the small intestine. These toxic effects of TFE were first observed at 8 to 16 hr after treatment, persisted for 96 hr, and were accompanied by severe diarrhea and edema of the small intestine. A non-lethal dose of TFE increased the sensitivity of rats to bacterial endotoxin lethality by approximately 1000-fold. Antibiotic and antiendotoxin pretreatment reduced the lethality of TFE from 80 to 20% of the rats, but did not prevent the other toxic effects of TFE. In vitro experiments with serum from TFE-pretreated rats (0.13 g/kg) supported the growth of an average of 65% fewer cultured bone marrow cell colonies compared to the number of colonies produced when serum from control rats was used. This suggests that TFE-induced bone marrow depression and leukopenia are related to a decrease in colony stimulating factor activity. Taken together these results explain the rapid development of lethal bacterial infections in TFE-treated rats. TFE-mediated damage to the small intestine combined with prolonged leukopenia decreases the resistance of the rat to endogenous pathogens leading to systemic bacterial infection. In addition, the increased sensitivity to endotoxin induced by TFE leads to lethal endotoxemia.

Subchronic oral toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin in the guinea pig: comparisons with a PCB-containing transformer fluid pyrolysate.

In contrast to the well-characterized acute toxicity of the environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD) in the guinea pig, the effects of prolonged po exposure in this species are unknown. The present report describes the results of administration to guinea pigs of 2,3,7,8-TCDD in the feed at levels of 0, 2, 10, 76, or 430 ppt for up to 90 days. Additional aims were to examine recovery following prolonged 2,3,7,8-TCDD exposure in the guinea pig and to generate data to facilitate comparison of the previously reported toxicity of a transformer fluid pyrolysate with that of pure 2,3,7,8-TCDD. Animals receiving 430 ppt 2,3,7,8-TCDD exhibited body weight loss, thymic atrophy, liver enlargement, and 60% mortality by Day 46 (males) and by Day 60 (females), when surviving animals in this group were sacrificed. Total 2,3,7,8-TCDD consumption was approximately 1.3 and 1.9 micrograms/kg, respectively. Animals receiving 76 ppt 2,3,7,8-TCDD for 90 days (total 0.44 microgram/kg) exhibited a decreased rate of body weight gain and increased relative (to body) liver weights. Male animals also displayed a reduction in relative thymus weights and elevated serum triglycerides, while females exhibited hepatocellular cytoplasmic inclusion bodies and lowered serum alanine aminotransferase activities. Toxic effects were generally similar to those observed after acute 2,3,7,8-TCDD administration. No dose-related alterations were seen in animals receiving either 10 ppt (total 0.06 micrograms/kg) or 2 ppt (total 0.01 micrograms/kg) for 90 days, establishing a no-observed-effect level of approximately 0.65 ng 2,3,7,8-TCDD/kg/day. In the recovery study, groups of guinea pigs were administered 430 ppt 2,3,7,8-TCDD for 11, 21, or 35 days and then allowed to recover for an additional 79, 69, or 55 days, respectively. Treatment-related mortality in each group was 0, 10, and 70%, respectively, by Day 90. An effective LD50 of 0.8 microgram 2,3,7,8-TCDD/kg for prolonged exposure was calculated on the basis of these results, a value lower than those previously reported from this laboratory for acute exposure. The results also suggested a possible lowering of the body weight "set point" following 2,3,7,8-TCDD exposure. Comparison of the present findings with those previously reported for a transformer fluid pyrolysate containing a mixture of polychlorinated aromatic species indicated both a greater variety of toxic effects and flatter dose-response relationships for the pyrolysate in the guinea pig.

Relationship between Ah receptor-mediated polychlorinated biphenyl (PCB)-induced humoral immunosuppression and thymic atrophy.

Thymic atrophy and humoral immunosuppression by certain polychlorinated biphenyls is associated with the aromatic hydrocarbon (Ah) receptor in mice. We examined the relationship between these two toxic effects. 3,3',4,4'-Tetrachlorobiphenyl (TCB), which causes immunosuppression and thymic atrophy, and 2,3,3',4,4',5-hexachlorobiphenyl, which causes immunosuppression without thymic atrophy, were administered i.p. to C57BL/6 mice at 0, 35 and 350 mumol/kg b.wt. 2 days before i.v. immunization with 10 micrograms of Escherichia coli lipopolysaccharide. Both congeners caused significant suppression of the day 4 anti-lipopolysaccharide plaque-forming cell response/spleen (less than or equal to 46% of control). TCB (350 mumol/kg) was also administered 2 days before either a primary or secondary i.p. immunization with sheep erythrocytes. TCB treatment before primary immunization had no effects on the day 5 secondary response, whereas treatment before the secondary immunization significantly inhibited both day 5 immunoglobulin M and immunoglobulin G plaque-forming cells (less than 10 and less than 2% of control, respectively) and decreased serum antibody. TCB administered either 8 or 2 days before or 2 or 4 days after immunization with sheep erythrocytes demonstrated that significant suppression of both plaque-forming cells and serum antibody could occur without thymic atrophy. Immunity was most impaired when TCB was given 2 days before immunization. These results demonstrate that thymic atrophy does not always accompany the severe immunosuppression caused by Ah receptor ligands and suggests that it may not be a sensitive measure of Ah receptor-mediated immunosuppression. The data also suggests that differentiation of B lymphocytes into antibody producing cells is impaired during Ah receptor-mediated gene activation.

Studies on the effect of low dose methotrexate on rat adjuvant arthritis.

Adjuvant arthritis in rats was induced by the intradermal administration of Freund's complete adjuvant. When these immunized rats were treated orally with low doses of methotrexate (150-600 micrograms/kg/week) a statistically significant suppression of paw inflammation was observed. This low dose of methotrexate was comparable to that used in the treatment of human rheumatoid arthritis (RA). Our results are the first demonstration of the efficacy of low dose methotrexate in an animal model of human RA.

Chemical and biological investigations of a transformer accident at Binghamton, NY.

A transformer fire occurred in a state office building in Binghamton, NY on February 5, 1981. Particulates from inside surfaces of ceiling panels on 16 of the 17 floors had concentrations of polychlorinated dibenzofurans (PCDFs) ranging from less than 1 part per million (ppm) to 1200 ppm while polychlorinated biphenyl (PCB) concentrations varied from 28 ppm to 23,000 ppm. In spite of the wide variations in contaminant concentrations, complete analytical data from 11 floors showed that there was a consistent PCDF/PCB ratio (0.067 +/- 0.026) and also consistent PCDF isomer group distributions (tetra-CDFs, 33 +/- 5%; penta-CDFs, 40 +/- 3%; hexa-CDFs, 18 +/- 7%; hepta-CDFs, 6 +/- 3%). It was found that the particulate samples could be successfully ranked in order of their degree of chemical contamination by an in vitro bioassay. The bioassay was based on induction of keratinization or changes in morphology in mouse epithelial cells. Animal toxicology experiments were carried out with a soot sample containing a PCDF concentration which approximated the mean value found on the ceiling particulates. The single dose oral LD values of the soot and its benzene extract equivalent, each administered to female guinea pigs in 0.75% methyl cellulose, were 410 and 327 mg/kg, respectively. These results demonstrated that the soot matrix had virtually no effect on the toxicity of the chemical contaminants in the soot. Morphological alterations in liver tissues from animals receiving the soot were found after examination by electron and light microscopy.(ABSTRACT TRUNCATED AT 250 WORDS)

Correlations between polychlorinated biphenyl immunotoxicity, the aromatic hydrocarbon locus, and liver microsomal enzyme induction in C57BL/6 and DBA/2 mice.

The suppression of the antibody response by polychlorinated biphenyls (PCB) in mice is dependent on the planarity of the PCB molecule and on the expression of the aromatic hydrocarbon (Ah) receptor. In this study, the hypothesis that this form of immunotoxicity is a consequence of the activation of the Ah gene complex and that other compounds which are Ah receptor ligands would also be immunotoxic was tested. 2,2',4,4'-Tetrachlorobiphenyl (TCB), 2,3,3',4,4',5-hexachlorobiphenyl (HCB), phenobarbital (PB), or beta-naphthoflavone (BNF) was given ip to either C57BL/6 (B6,Ahb/Ahb) or DBA/2 (D2, Ahd/Ahd) mice 2 days before immunization with sheep erythrocytes. Organ weights, histopathology, hemagglutinating antibody titers, and the splenic direct antibody plaque-forming cell (PFC) response were evaluated on Day 5. Hepatic aryl hydrocarbon hydroxylase (AHH) induction by these compounds and by 2,2',5,5'-TCB and 3,3',4,4'-TCB was measured as an indicator of Ah receptor binding and subsequent activation of the Ah gene complex by methylcholanthrene-type inducers, while aminopyrine N-demethylase (APND) was measured as an indicator of PB-type induction. 2,2',4,4'-TCB and PB had no effects on the immune parameters of either strain but induced APND activity in both strains. 2,2',5,5'-TCB slightly induced APND activity in B6 mice. 2,3,3',4,4',5-HCB caused a 70% suppression of PFC per spleen, decreased the serum antibody titer, elevated cytochrome P-450 levels (193%), induced both APND (165%) and AHH (217%) activity in B6 mice, but it induced only APND (156%) activity in D2 mice. 3,3',4,4'-TCB elevated cytochrome P-450 levels (210%) and induced both APND (129%) and AHH (321%) activities in B6 mice but only increased APND activities (115%) in D2 mice. BNF elevated cytochrome P-450 (144%), caused a 49% suppression in PFC per spleen, and induced both APND (156%) and AHH (248%) activities but only in B6 mice. These results support the hypothesis that the immunotoxicity caused by halogenated and polycyclic aromatic hydrocarbons is a consequence of activation of the Ah gene complex and suggests that this toxic effect can be initiated by any Ah receptor ligand.

Subchronic exposure of mice to Love Canal soil contaminants.

The health hazard potential of soil collected from the surface of the Love Canal chemical dump site in Niagara Falls, New York, was assessed in 90-day exposure studies. Female CD-1 mice were exposed to two concentrations of the volatile components of 1 kg of soil with and without direct soil contact. Control mice were identically housed but without soil. The soil was replaced weekly and 87 compounds were detected in the air in the cages above fresh and 7-day-old soil as analyzed by gas chromatography/mass spectrometry. The concentration of many of these compounds decreased during the 7-day exposure cycle. Histopathologic, hematologic, and serum enzyme studies followed necropsy of all mice. There was no mortality of mice exposed for up to 90 days under any condition. Thymus and spleen weights relative to body weight were increased after 4 weeks of exposure by inhalation but not after 8 or 12 weeks of exposure. alpha-, beta-, and delta- Benzenehexachlorides , pentachlorobenzene, and hexachlorobenzene were detected in liver tissue from these animals. Mice exposed to 5- to 10-fold elevated concentration of volatiles had increased body and relative kidney weights. There was no chemically induced lesion in any animal exposed only to the volatile soil contaminants. Mice exposed by direct contact with the soil without elevated volatile exposure had increased body (10%) and relative liver weights (169%). Centrolobular hepatocyte hypertrophy, which involved 40 to 70% of the lobules, was observed in all mice in this group.(ABSTRACT TRUNCATED AT 250 WORDS)