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Nigel J Walker

Publications and source records attributed to Nigel J Walker.

6 recordsLinked to original sources

Area under the curve as a dose metric for promotional responses following 2,3,7,8-tetrachlorodibenzo-p-dioxin exposure.

An underlying basis of risk assessment is that an equivalent risk for a specified dose metric exists that allows for extrapolation of dose-response relationships between species. To better understand the use of area under the curve (AUC) as a dose metric for complex biological responses following 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure, a study was designed using a physiologically based pharmacokinetic model in the female Sprague-Dawley rat that would result in equivalent AUCs of total liver TCDD with differing patterns of exposure. In the first group, rats received a high peak dose of 3500 ng TCDD/kg twice per week in the first week followed by a lower TCDD dose of 81 ng/kg twice per week for the remainder of the study. In the second group, rats received a gavage dose of 350 ng TCDD/kg in corn oil twice per week for the study duration of 15 weeks. Age-matched control rats received corn oil as a vehicle control. Placental glutathione S-transferase (PGST)-positive foci were measured in representative liver lobes by immunohistochemistry, as a representative complex biological response resulting from TCDD exposure. The median volume fraction was 0.045% in control rats and was significantly elevated in TCDD treatment groups. However, the volume fraction of PGST-positive foci was significantly higher in the TCDD group given the high peak dose during the first week of TCDD treatment compared with the group receiving the same average daily dose over the study duration: 0.74 versus 0.20%, respectively. These findings suggest that the peak magnitude of TCDD in liver rather than AUC may play a significant role in the induction of complex biological responses by TCDD.

Animals↗

Effects of TCDD upon IkappaB and IKK subunits localized in microsomes by proteomics.

Biochemical studies have shown that microsomes represent an important subcellular fraction for determining 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) effects. Proteomic analysis by two-dimensional gel-mass spectrometry of liver microsomes was undertaken to gain new insight into the actions of TCDD in male and female rats. Proteomic analysis showed TCDD induced several xenobiotic metabolism enzymes as well as a protein at 90kDa identified by mass spectrometry as IkappaB kinase beta/IKK2. This observation led to the discovery of other NF-kappaB binding proteins and kinases in microsomes and effects by TCDD. Western blotting for IKK and IkappaB family members in microsomes showed a distinct pattern from cytosol. IKK1 and IKK2 were both present in microsomes and were catalytically active although, unlike cytosol, IKKgamma/NEMO was not detectable. TCDD exposure produced an elevation in cytosolic and microsomal IKK activity of both genders. The NF-kappaB binding proteins IkappaBbeta and IkappaBgamma were prevalent in microsomes, while IkappaBalpha and IkappaB epsilon proteins were absent. TCDD treatment produced hyperphosphorylation of microsomal IkappaBbeta in both sexes with females being most sensitive. In cytosol, IkappaBalpha, IkappaBbeta, and IkappaB epsilon, but not IkappaBgamma, were clearly observed but were not changed by TCDD. Overall, proteomic analysis indicated the presence of NF-kappaB pathway members in microsomes, selectively altered by dioxin, which may influence immune and inflammatory responses within the liver.

Animals↗

Impact of physiologically based pharmacokinetic modeling on benchmark dose calculations for TCDD-induced biochemical responses.

In risk assessment, noncancer risk is currently estimated using a no observed adverse effect level (NOAEL) from an experimental dose-response study, divided by uncertainty factors, to estimate a presumably safe level of human exposure. A benchmark dose approach, in which an effective dose (ED) resulting in a specified percentage increase over background for effects is estimated by empirical modeling, has been proposed as a replacement for the NOAEL methodology. The aim of this analysis is to compare methods for estimation of body burden resulting in a 1 or 10% maximum increase over background (BB(01) or BB(10)) for biochemical responses following exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in female Sprague-Dawley rats. In one method, an ED resulting in a prespecified increase in response over background was estimated using average daily doses and an empirical Hill model. The ED was then converted to an equivalent body burden by a simple kinetic model assuming steady-state conditions, half-life of TCDD in the rat, and 100% absorption of TCDD. Alternatively, a mechanistic physiologically based pharmacokinetic (PBPK) model of TCDD in the rat was used to predict body burdens for administered doses. These PBPK-modeled body burdens were then used directly by the Hill model to calculate a BB(01) or BB(10). In general, the body burden values derived from EDs were within five-fold of BB(01) or BB(10) calculated from the PBPK model. BB(01) and BB(10) values from both methods were within two orders of magnitude of current human general population exposure to all dioxin-like compounds.

Animals↗

Promotion of altered hepatic foci by 2,3,7,8-tetrachlorodibenzo-p-dioxin and 17beta-estradiol in male Sprague-Dawley rats.

The determination of differences in hormonal regulation of tumor promotion-related response to 2,3,7,8-tetrachlorodibenzop-dioxin (TCDD) between males and females may identify factors contributing to the female-specific hepatocarcinogenicity of TCDD in rats. In the current study, diethylnitrosamine-initiated male Sprague-Dawley rats were exposed to TCDD or corn oil vehicle in the presence and absence of 17beta-estradiol (E2), and cell proliferation and development of preneoplastic altered hepatic foci (AHF) were determined. After 30 weeks of exposure, gamma-glutamyltranspeptidase (GGT)-positive AHF and the number of placental glutathione-s-transferase (PGST)-positive AHF were significantly higher in TCDD-treated rats than in control rats. Both the number and volume fraction of GGT-positive AHF were significantly lower in rats cotreated with E2 regardless of TCDD exposure compared with corresponding non-E2-treated groups and were unaffected by TCDD. In contrast, the number of PGST-positive AHF was significantly higher in E2-treated rats in the absence of TCDD treatment. In addition, whereas E2 had no effect on the volume fraction of PGST-positive foci, the levels in rats cotreated with both E2 and TCDD were significantly higher than in controls. No differences were observed in cell proliferation between TCDD-treated and control rats, although cell proliferation was lower in rats exposed to E2 compared with placebo controls. The weaker potency of tumor promotion and lack of induction of cell replication and DNA damage in male rats likely explain the female-specific hepatocarcinogenicity of TCDD in chronic bioassays.

Animals↗

Differential toxicogenomic responses to 2,3,7,8-tetrachlorodibenzo-p-dioxin in malignant and nonmalignant human airway epithelial cells.

In humans, exposure to high levels of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is associated with chronic obstructive pulmonary disease and lung cancer. While several studies have shown that the lung is a target organ for TCDD toxicity, little is known on the specific biological pathways altered by TCDD. Studies have shown that the transcriptional response of TCDD (in vivo and in vitro) is complex, and exhibits cell type and tissue specificity. Thus, the purpose of this study was to look at global and concentration-dependent effects of TCDD on gene expression in human lung cells. Gene expression profiling of both a nontumorigenic (HPL1A) and a malignant, tumorigenic lung cell line (A549) was performed by microarray dual fluorescence hybridizations in cells treated with increasing concentrations of TCDD (0, 0.1, 1, 10 nM) for 24 h. Real time RT-PCR was used to verify alterations in specific genes. Results showed that 68 out of 2091 genes were changed in each cell line, and 15 of those genes were found altered in both cell lines. Common gene responses altered by TCDD were identified and included known xenobiotic metabolizing genes, genes known to alter cell cycle, as well as genes that are involved with cell signaling and that mediate cell motility or communication. Cell line specific differences in gene expression were found that indicate the nonmalignant HPL1A cells are retinoic acid responsive. In addition, TCDD altered specific immunomodulatory genes in the HPL1A cells. These data show that TCDD alters multiple integrated networks of signaling pathways associated with pulmonary disease, particularly that of lung cancer.

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