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L Howie

Publications and source records attributed to L Howie.

9 recordsLinked to original sources

Relative sensitivities of 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced Cyp1a-1 and Cyp1a-2 gene expression and immunotoxicity in female B6C3F1 mice.

Improvements in risk assessment require better linkage of exposure to response by the determination of target tissue dose. The relative sensitivity of several responses in female B6C3F1 mice was compared on the basis of administered and target tissue dose spanning 3 orders of magnitude. Twenty-four hours after administration, [3H]TCDD was detected in the heart, spleen, kidney, uterus, thymus, lung, and liver, and the highest concentrations were noted in the liver, uterus, and lung. At doses from 5 to 25 ng/kg, hepatic [3H]TCDD levels associated with the cytosolic and nuclear subcellular fractions increased from 12 to 62% of the total liver levels and then decreased at higher doses. At the two lowest doses used in the enzyme induction study, 5 and 10 ng/kg, the levels of specifically bound nuclear Ah receptor complex liganded with [3H]TCDD were 2.3 and 2.5 fmol/mg protein. Slightly higher levels of nuclear Ah receptor complex were observed at doses between 25 and 100 ng/kg (i.e., 3.6 to 4.2 fmol/mg protein) and a steep dose-dependent increase in nuclear Ah receptor levels was noted at doses of 500, 1000, and 5000 ng/kg (8.0, 39.3, and 92.8 fmol/mg protein, respectively). The dose-dependent effects of [3H]TCDD on hepatic Cyp1a-1 and Cyp1a-2 mRNA levels, ethoxyresorufin O-deethylase (EROD) activity, and the splenic antibody plaque-forming cell (PFC) response to sheep red blood cells were also determined; the latter response was determined 9 days after administration of TCDD. Statistically significant induction of hepatic Cyp1a-1 was observed at lower doses (25 ng/kg) than any other marker, followed by induction of EROD and PFCs expressed per spleen or per 10(6) cells which was observed at 100 ng TCDD/kg and at higher doses. Cyp1a-2 was elevated significantly relative to control at doses > or = 1000 ng/kg. The ED50 value for PFCs/10(6) cells was the lowest of the variables analyzed and was not statistically significantly different from control (91 +/- 92 ng/kg). A 50% increase in Cyp1a-2 and Cyp1a-1 mRNA levels was observed at doses of 736 +/- 132 and 1630 +/- 431 ng/kg, respectively. Due to variability in response in PFCs/spleen and the submaximal induction of EROD activity, ED50 values could not be calculated for these responses. The analyses indicate that the immunosuppressive response (when normalized for the number of spleen cells) may be depressed by administered doses as low as 90 ng TCDD/kg body weight. A 50% increase in Cyp1a-1 or Cyp1a-2 was observed at higher administered doses (1630 or 736 ng/kg, respectively.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗

Immunosuppressive effects of highly chlorinated biphenyls and diphenyl ethers on T-cell dependent and independent antigens in mice.

The dose-dependent effects of 2,2',3,3',4,4',5,5',6-nonachlorobiphenyl (nonaCB), 2,2',3,3',4,4',5,6,6'-nonaCB, 2,2',3,3',4,5,5',6,6'-nonaCB and decaCB on the suppression of the splenic plaque-forming cell (PFC) response to the T-cell-dependent antigen, sheep red blood cells (SRBCs) and the T-cell-independent antigen, trinitrophenyl-lipopolysaccharide (TNP-LPS), were determined in genetically inbred mice. In addition, the induction of hepatic microsomal ethoxyresorufin O-deethylase (EROD) activity was also measured. The highly chlorinated biphenyls suppressed the splenic PFC response to SRBCs in C57BL/6 and DBA/2 mice and were relatively more active in the former strain. The C57BL/6 mice are more responsive to aryl hydrocarbon (Ah) receptor agonists than DBA/2 mice and these data support a possible role for the Ah receptor in mediating this response. However, previous studies with polychlorinated biphenyls (PCBs) indicate that congeners with 3 or 4 ortho-chloro substituents are inactive as Ah receptor agonists and this was consistent with the minimal induction of hepatic microsomal EROD activity by the highly chlorinated biphenyls in both strains of mice. Thus, the results suggest that the inhibition of the splenic PFC response to SRBCs observed in this study was primarily an Ah receptor-independent response. Some of the highly chlorinated diphyenyl ethers namely decachlorodiphenyl ether and 2,2',3,3',4,4',5,6,6'-nonachlorodiphenyl ether, inhibited the antigenic response to TNP-LPS in C57 BL/6 mice. The results indicate that the suppression of the TNP-LPS-mediated immune response may be a more reliable indicator of the Ah receptor-dependent immunotoxicity of halogenated hydrocarbons.

Animals↗

Teratogenicity and immunotoxicity of 3,3',4,4',5-pentachlorobiphenyl in C57BL/6 mice.

Administration of 3,3',4,4',5-pentachlorobiphenyl (pentaCB) to female C57BL/6 mice at doses from 130.5 to 522 micrograms/kg body weight resulted in the dose-dependent formation of fetal cleft palate and hydronephrosis. The estimated relative potency of 3,3',4,4',5-pentaCB compared to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was in the range of < 0.07-0.04. The immunotoxicity of 3,3',4,4',5-pentaCB and two structurally-related congeners, 3,3',4,4'-tetraCB and 3,3',4,4',5,5'-hexaCB, was investigated in male C57BL/6 mice by determining their suppression of the splenic plaque-forming cell response to sheep red blood cells. The potencies of these compounds relative to TCDD were determined from the ratios of their corresponding ED50 values and were 0.77-0.55 (3,3',4,4',5-pentaCB), 1.1-0.29 (3,3',4,4',5,5'-hexaCB) and 0.14-0.03 (3,3',4,4'-tetraCB). These results demonstrate that the immunosuppressive activities of the PCB congeners relative to TCDD were much higher than observed for many other TCDD-like responses in mice and other laboratory animals.

Abnormalities, Drug-Induced↗

Immunosuppressive and monooxygenase induction activities of highly chlorinated diphenyl ether congeners in C57BL/6 and DBA/2 mice.

The dose-response effects of 2,2',3,3',4,5,5',6,6'-2,2',3,3',4,4',5,6,6'- and 2,2',3,3',4,4',5,5',6- nonachlorodiphenyl ether (non-aCDE) and decachlorodiphenyl ether (decaCDE) on the splenic plaque-forming cell (PFC) response to sheep red blood cells (SRBCs) and the induction of hepatic microsomal ethoxyresorufin O-deethylase (EROD) activity was determined in aryl hydrocarbon (Ah)-responsive C57BL/6 and less Ah-responsive DBA/2 mice. All the congeners exhibited immunotoxicity at doses between 2.5 and 10 mumol/kg in C57BL/6 mice whereas in DBA/2 mice doses > or = 25 mumol/kg were required to cause inhibition of the PFC response to SRBCs. The results also showed that the nonaCDE isomers and decaCDE were more active as inducers of hepatic EROD activity in C57BL/6 than DBA/2 mice; however, there was not a correlation between the induced EROD activity and the CYP1A1 and CYP1A2 mRNA levels in the C57BL/6 mice. These data suggested that the immunotoxicity of these compounds was mediated through the Ah receptor. However, the results showed that the immunotoxicity of the nonaCDE isomers and decaCDE was unexpectedly high compared to that of lower chlorinated diphenyl ethers and there were no apparent structure-activity relationships among the higher chlorinated congeners. This suggests that some of the immunosuppressive effects observed for the nonaCDE isomers and decaCDE may be Ah receptor-independent.

Animals↗

The effect of 6-nitro-1,3,8-trichlorodibenzofuran as a partial estrogen in the female rat uterus.

Administration of 6-nitro-1,3,8-trichlorodibenzofuran (6-NCDF) caused a dose- and time-dependent increase in uterine wet weight and cytosolic and nuclear estrogen receptor (ER) and progesterone receptor (PR) levels in immature female Sprague-Dawley rats. These estrogenic effects persisted for up to 96 or 144 hr after initial administration of 6-NCDF and could be observed at a dose as low as 2 mumol/kg. In contrast, 6-NCDF (25 mumol/kg) did not increase rat uterine peroxidase activity or epidermal growth factor (EGF) receptor binding activity. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD), which exhibits a broad spectrum of antiestrogenic effects in the female rat uterus, inhibited the 17 beta-estradiol-induced increase in uterine wet weights, cytosolic and nuclear ER and PR levels, peroxidase activity, and EGF receptor binding activity. In contrast, 2,3,7,8-TCDD inhibited the uterotropic effects caused by 6-NCDF but did not affect the 6-NCDF-induced uterine ER and PR levels. 6-NCDF is a weak inducer of hepatic microsomal ethoxyresorufin O-deethylase activity and competitively binds to the aryl hydrocarbon (Ah) receptor but not the PR or ER. Thus both 6-NCDF and 2,3,7,8-TCDD, two ligands which bind to the Ah receptor, exhibit both partial estrogenic and antiestrogenic properties and serve as useful models for delineating the complex biochemical interactions between the ER and Ah receptor signal transduction pathways.

Animals↗

Immunosuppressive and monooxygenase induction activities of polychlorinated diphenyl ether congeners in C57BL/6N mice: quantitative structure-activity relationships.

The dose-response effects of several polychlorinated diphenyl ether (polyCDE) congeners on the inhibition of the splenic plaque-forming cell (PFC) response to sheep red blood cell antigen and the induction of hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities were determined in male C57BL/6 mice. The immunotoxic potencies for the polyCDE congeners (ED50 values for the suppression of PFCs/spleen and PFCs/10(6) cells) followed the order 2,3,3',4,4',5-hexaCDE (0.5 and 2.2 mumols/kg) greater than 3,3',4,4',5-pentaCDE (8.8 and 5.1 mumols/kg) greater than 2,3',4,4',5-pentaCDE (21.8 and 14.2 mumols/kg) greater than 3,3',4,4'-tetraCDE (50.6 and 28.7 mumols/kg) greater than 2,2',4,4',5,5'-hexaCDE (81.2 and 56.5 mumols/kg) greater than 2,2',4,5,5'-pentaCDE (258 and 228 mumols/kg) greater than 2,2',4,4',5,6'-hexaCDE (greater than 400 mumols/kg for both responses). The potencies of the polyCDE congeners as inducers of hepatic microsomal AHH and EROD activities were similar to their immunotoxicities and only one compound, namely, 2,3',4,4',5,5'-hexaCDE, did not cause dose-response immunosuppressive effects in the mice. The structure-activity relationships for the polyCDEs exhibited both differences and similarities. For example, the coplanar 3,3',4,4'-tetraCDE and 3,3',4,4',5-pentaCDE congeners were less immunotoxic than their monoortho 2,3',4,4',5-pentaCDE and 2,3,3',4,4',5-hexaCDE analogs, respectively, and similar results were also observed for their enzyme induction potencies. For the corresponding polychlorinated biphenyls (PCB) congeners the coplanar compounds were significantly more active than their monoortho analogs. In addition, two diortho-substituted compounds, namely, 2,2',4,5,5'-pentaCDE and 2,2',4,4',5,5'-hexaCDE, were also immunotoxic at a dose of 400 mumols/kg whereas, their PCB analogs were inactive. These studies clearly demonstrate that for the polyCDE congeners, increasing ortho-chloro substitution is less effective in reducing the activity of these congeners compared to the well-recognized ortho effects reported for the PCBs. The differences in the structure-activity relationships between polyCDEs and PCBs are related to the ether bridge in the polyCDEs in which the resultant increased bond length between the two phenyl rings thereby diminishes the effects of ortho substituents on the biochemical and toxic potencies of these compounds.

Animals↗

The structure-dependent effects of heptachlorodibenzofuran isomers in male C57BL/6 mice: immunotoxicity and monooxygenase enzyme induction.

The dose-response effects of the 1,2,3,4,6,7,8-, 1,2,3,4,7,8,9-, 1,2,3,4,6,8,9-, and 1,2,3,4,6,7,9-heptachlorodibenzofurans (HpCDFs) on the splenic plaque-forming cell (PFC) response to sheep erythrocytes and on the induction of hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin-O-deethylase (EROD) activities were determined in male C57BL/6 mice. The ED50 values for the decrease in the PFCs/spleen, the number of PFCs/10(6) viable cells, and the induction of AHH and EROD activities were 1,2,3,4,6,7,8-HpCDF, 0.011, 0.018, 0.11, and 0.315 mumol/kg, respectively; 1,2,3,4,7,8,9-HpCDF, 0.012, 0.054, 0.70, and 0.20 mumol/kg, respectively; 1,2,3,4,6,7,9-HpCDF, 1.2, 1.3, greater than 43, and greater than 43 mumol/kg, respectively; 1,2,3,4,6,8,9-HpCDF, 1.5, 3.4, 22, and 22 mumol/kg, respectively. It was apparent from these studies that the 2,3,7,8-substituted HpCDF isomers (1,2,3,4,6,7,8- and 1,2,3,4,7,8,9-) were significantly more potent than the compounds which contained only three lateral C1 groups. These results were obtained using a multiple dosing regimen in which 10 separate doses of the HpCDF isomers were administered to the mice by intraperitoneal injection over a period of 12 days. However, when the mice were treated with a single dose of an HpCDF congener, which was equivalent to the total dose used in the multiple dose study, the responses were comparable. A comparison of the relative immunotoxic potencies of the 2,3,7,8-substituted HpCDFs and 2,3,7,8-tetrachlorodibenzo-p-dioxin showed that the latter compound was approximately 10 times more active than the HpCDFs.

Animals↗