Faculty Bibliography

The organochlorine pesticide methoxychlor (MXC) is an environmental estrogen known to stimulate the expression of the egg-yolk protein, vitellogenin (Vtg) in fish species. To begin to understand the underlying mechanisms for how MXC exerts its deleterious effects on the endocrine system, male largemouth bass (Micropterus salmoides) were treated with 2.5, 10, or 25mg/kg MXC and compared to fish pair-treated with 1mg/kg 17 beta-estradiol (E2), and vehicle control. Fish were sacrificed 24, 48, or 72 h following treatment. The liver and testes were then assayed for changes in expression of the three bass estrogen receptors (ERs alpha, beta a, and beta b) in tissues, as well as Vtg and cytochrome P450 (CYP) 3A isoform 68 in the liver and steroidogenic acute regulatory protein (StAR) in the testes. In the liver, significant increases in gene expression were seen for each of the genes measured by 24 h and each returned to the level of the vehicle by 72 h. Total testosterone 6 beta-hydroxylase activity, reflective of CYP3A activity, was also increased by 24h for all of the exposures. In the testes, ER alpha was unaffected by any treatment, ERbetaa was up-regulated only by MXC, peaking at 24h for the 2.5 and 10mg/kg MXC and at 48 h for the 25mg/kg MXC treatment. By 72 h, the MXC effects had disappeared, while E2 significantly decreased the expression of ER beta a mRNA. ER beta b expression in the testes was stimulated by all concentrations of MXC by 24 h and the effect remained up to 72 h, whereas E2 had no effect. Finally, StAR expression was also found to be decreased by E2 and all MXC treatments. However, the effect on StAR expression by E2 occurred within 24h, while the effect by all concentrations of MXC was not seen until 72 h after treatment. The stimulatory effects of E2 and 25mg/kg MXC on the expression of the ERs in the liver were opposite to the responses seen in the testes, suggesting an inverted relationship between these two tissue types. These results provide a possible mechanism showing that alterations in reproductive signaling in male fish by xenoestrogens not only increase Vtg expression in the liver, but may also decrease reproductive success by muting some of the estrogen signals required for sperm production.

The purpose of this study was to determine the mechanisms by which the pesticide, methoxychlor (MXC), acts as an environmental endocrine disruptor through interaction with the three largemouth bass (Micropterus salmoides) estrogen receptors (ERs) alpha, betaa, and betab. MXC is a less-environmentally persistent analog of DDT that behaves as a weak estrogen. Using transient transfection assays in HepG2 cells, we have previously shown that each receptor is responsive to the endogenous ligand 17beta-estradiol (E(2)) in a dose-dependent manner. The parent compound, MXC, showed dose-dependent stimulation of transcriptional activation through all three ERs. In addition to the parent molecule, each of the metabolites was also estrogenic with all three ERs. The order of potency for ERalpha and ERbetab was HPTE>OH-MXC>MXC, while the opposite order was seen for ERbetaa. HepG2 cells did not substantially metabolize MXC to the active metabolites, thus the activity of MXC was not due to metabolism. When examining the effects of increasing concentrations of MXC at a fixed concentration of E(2), all three ERs show increased activity compared to that with E(2) alone, showing that the effects of MXC and E(2) are additive. However, when this experiment was repeated with increasing concentrations of HPTE at a fixed concentration of E(2), the activity of ERalpha was decreased, that of ERbetab was increased, while that of ERbetaa was unaffected compared to E(2) alone. These experiments suggest that HPTE functions as an E(2) antagonist with ERalpha, an E(2) agonist with ERbetab and does not perturb E(2) stimulation of ERbetaa. While it is clear the ERbeta subtypes are the products of different genes (due to a gene duplication in teleosts) the differences in their responses to MXC and its metabolites indicate that their functions diverge, both in their in vivo molecular response to E(2), as well as in their interaction with endocrine disrupting compounds found in the wild.

The method we describe in this chapter describes the synthesis and use of cDNA macroarrays for determining changes in gene expression due to environmental toxicants as well as the methods and materials that are required to do this work. While the details are for investigators working with nontraditional species for which commercial arrays are unavailable, anyone can design and use their own custom arrays using these protocols. We have intentionally left out details for statistical analysis for the arrays as the methods for doing this are still being developed and would need to be specific to the experiment being done. In all, gene macroarrays are a relatively easy way to generate large amounts of data in a short amount of time.

The estrogen receptor (ER) signaling cascade is a vulnerable target of exposure to environmental xenoestrogens, like nonylphenol (NP), which are causally associated with impaired health status. However, the impact of xenoestrogens on the individual receptor isotypes (alpha, beta a, and beta b) is not well understood. The goal of these studies was to determine the impact of NP on largemouth bass (Micropterus salmoides) ER isotype expression and activity. Here, we show that hepatic expression levels of three receptors are not equivalent in male largemouth bass exposed to NP by injection. Transcript levels of the ER alpha subtype were predominantly induced in concert with vitellogenin similarly to fish exposed to 17beta-estradiol (E(2)) as measured by quantitative real-time PCR. NP also induced circulating plasma levels of estrogen, which may contribute to overall activation of the ERs. To measure the activation of each receptor isotype by E(2) and NP, we employed reporter assays using an estrogen response element (ERE)-luciferase construct. Results from these studies show that ER alpha had the greatest activity following exposure to E(2) and NP. This activity was inhibited by the antagonists ICI 182 780 and ZM 189 154. Furthermore, both beta b and beta a subtypes depressed ER alpha activation, suggesting that the cellular composition of receptor isotypes may contribute to the overall actions of estrogen and estrogenic contaminants via the receptors. Results from these studies collectively reveal the differential response of fish ER isotypes in response to xenoestrogens.

Gene arrays provide a powerful method to examine changes in gene expression in fish due to chemical exposures in the environment. In this study, we expanded an existing gene array for sheepshead minnows (Cyprinodon variegatus) (SHM) and used it to examine temporal changes in gene expression for male SHM exposed to 100 ng 17beta-estradiol (E(2))/L for five time points between 0 and 48 hr. We found that in addition to the induction of genes involved in oocyte development (vitellogenin [VTG], zona radiata [ZRP]), other genes involved in metabolism and the inflammatory response are also affected. We identified five patterns of temporal induction in genes whose expression was modified due to E(2) exposure. We validated the gene array data for the expression of VTG 1, VTG 2, ZRP 2 and ZRP 3 and found that with low levels of exogenous E(2) (100 ng E(2)/L) exposure, ZRP expression precedes VTG expression. However, at higher concentrations of E(2) (500 ng E(2)/L), the difference in temporal expression appears to be lost. Exposure to high levels of environmental contaminants may affect the normal ordered expression of genes required for reproduction. Gene expression profiling using arrays promises to be a valuable tool in the field of environmental toxicology. As more genes are identified for species used in toxicological testing, researchers will be better able to predict adverse effects to chemical exposures and to understand the relationships between changes in gene expression and changes in phenotype.

The regulation of insulin-like growth factor-binding protein-2 (IGFBP-2) gene transcription in specific cell and developmental contexts is not well understood. Here, we identified DNA regions that mediate IGFBP-2 gene transcription in two of the three major cell types of the uterine endometrium of the early pregnant pig. Two clusters of transcriptional start sites at nucleotides -109/-105 and -96/-87 (+1, translational initiation site) in the porcine IGFBP-2 gene were localized in uterine endometrium and in primary cultures of endometrial glandular epithelial (GE) and stromal (ST) fibroblastic cells. Upstream regions of this gene (spanning -1,397/+73) were fused to a luciferase reporter gene, and the constructs were transiently transfected into endometrial GE and ST cells representative of pregnancy days 12 and 18 (day 115 = parturition). A short (110 bp) upstream region (-874/-765) stimulated the IGFBP-2 and heterologous SV40 promoters in the two cell types at both pregnancy days. Two noncontiguous copies of the novel sequence motif TCAGGG within the 110-bp fragment were implicated in transcriptional activity, since block mutation of these sequences led to a repression of SV40 basal promoter activity in endometrial cells. Southwestern blotting identified an endometrial nuclear protein of 34-kDa molecular weight that bound an oligonucleotide containing this motif, and EMSA suggested robust expression of this protein in early pregnancy endometrium and in ovary but at much reduced levels in endometrium at later pregnancy. A pair of E-box elements (CANNTG) within the 110 bp region was stimulatory to IGFBP-2 promoter activity; block mutation of these converted the 110-bp region into a potent transcriptional silencer in all but day 18 ST cells. Results identify novel DNA motifs that regulate the IGFBP-2 gene promoter in uterine endometrium in pregnancy-associated fashion.

In this study male largemouth bass (LMB) were exposed to the naturally occurring androgens, dihydrotestosterone (DHT) or 11-ketotestosterone (11-KT) in order to identify genes that are differentially regulated by these steroid hormones. Using subtractive hybridization on livers of fish treated with DHT against vehicle control, many novel LMB genes were cloned. These genes were added to our gene library and arrayed. Six genes were up-regulated and five were down-regulated by both androgens. But, each androgen also regulated specific genes. One gene that was identified as a potential androgen marker was spermidine-spermine-N(1)-acetyltransferase that was up-regulated by both androgens. Determining which genes are responsive to natural androgens will help to identify biochemical pathways that are impacted.

The Sp/KLF transcription factor basic transcription element-binding protein (BTEB1) regulates gene transcription by binding to GC-rich sequence motifs present in the promoters of numerous tissue-specific as well as housekeeping genes. Similar to other members of this family, BTEB1 can act as a transactivator or transrepressor depending on cell and promoter context, although the molecular mechanism underlying these distinct activities remains unclear. Here we report that BTEB1 can mediate signaling pathways involving the nuclear receptor for the steroid hormone progesterone in endometrial epithelial cells by its selective interaction with the progesterone receptor (PR) isoforms, PR-A and PR-B. Functional interaction with ligand-activated PR-B resulted in superactivation of PR-B transactivity, facilitated the recruitment of the transcriptional integrator CREB-binding protein within the PR-dimer, and was dependent on the structure of the ligand bound by PR-B. By contrast, BTEB1 did not influence agonist-bound PR-A transactivity, although it augmented PR-A inhibition of PR-B-mediated transactivation as well as potentiated ligand-independent PR-A transcriptional activity in the presence of CREB-binding protein. We also demonstrate similar positive modulatory actions of BTEB1-related family members Kruppel-like family (KLF) 13/FKLF2/BTEB3 and Sp1 on PR-B transactivity. Further, we provide support for the potential significance of the selective functional interactions of PR isoforms with BTEB1 in the peri-implantation uterus using mouse and pig models and in the breast cancer cell lines MCF-7 and T47D. Our results suggest a novel mechanism for the divergent physiological consequences of PR-A and PR-B on progesterone-dependent gene transcription in the uterus involving select KLF members.