Irvin R. Schultz

Dietary exposure to 2,2´,4,4´-Tetrabromodiphenyl Ether (PBDE-47) alters thyroid status and thyroid hormone–regulated gene transcription in the pituitary and brain

Background Polybrominated diphenyl ether (PBDE) flame retardants have been implicated as disruptors of the hypothalamic-pituitary-thyroid axis. Animals exposed to PBDEs may show reduced plasma thyroid hormone (TH), but it is not known whether PBDEs impact TH-regulated pathways in target tissues. Objective We examined the effects of dietary exposure to 2,2′,4,4′-tetrabromodiphenyl ether (PBDE-47)—commonly the highest concentrated PBDE in human tissues—on plasma TH levels and on gene transcripts for glycoprotein hormone α-subunit (GPHα) and thyrotropin β-subunit (TSHβ) in the pituitary gland, the autoinduced TH receptors α and β in the brain and liver, and the TH-responsive transcription factor basic transcription element-binding protein (BTEB) in the brain. Methods Breeding pairs of adult fathead minnows (Pimephales promelas) were given dietary PBDE-47 at two doses (2.4 μg/pair/day or 12.3 μg/pair/day) for 21 days. Results Minnows exposed to PBDE-47 had depressed plasma thyroxine (T4), but not 3,5,3′-triiodothyronine (T3). This decline in T4 was accompanied by elevated mRNA levels for TStHβ (low dose only) in the pituitary. PBDE-47 intake elevated transcript for TH receptor αin the brain of females and decreased mRNA for TH receptor β in the brain of both sexes, without altering these transcripts in the liver. In males, PBDE-47 exposure also reduced brain transcripts for BTEB. Conclusions Our results indicate that dietary exposure to PBDE-47 alters TH signaling at multiple levels of the hypothalamic-pituitary-thyroid axis and provide evidence that TH-responsive pathways in the brain may be particularly sensitive to disruption by PBDE flame retardants.

Dose-response relationships and pharmacokinetics of vitellogenin in rainbow trout after intravascular administration of 17α-ethynylestradiol

Abstract A commonly used endpoint in bioassays testing the estrogenicity of chemicals is the induction of the egg yolk precursor vitellogenin (VTG) in male fish. However, relatively little is known about the kinetics of induction and elimination of VTG in fish exposed to xenoestrogens. In this study, we administered graded intra-arterial doses (0.001, 0.1, 1.0 and 10.0 mg/kg) of 17α-ethynylestradiol (EE 2 ) to male rainbow trout via a dorsal aortic cannula which allowed repetitive blood sampling from individual fish for up to 48 days after injection. The plasma concentrations of VTG was quantified using an enzyme-linked immunosorbent assay procedure and the simultaneous concentrations of EE 2 were determined by gas chromatography-mass spectrometry. The pattern of VTG induction was similar for all doses of EE 2 , with a 12-h lag-time before increase from basal levels (0.006–0.008 μg/ml), then increasing sharply to maximum levels within 7–9 days ( C max =0.05, 711, 1521 and 2547 μg/ml VTG for the 0.001, 0.1, 1.0 and 10.0 mg/kg doses, respectively). After induction by EE 2 , VTG declined mono-exponentially with an elimination half-life of 42–49 h. The half-life of VTG increased to 145 h in the 10 mg/kg treated fish. The pharmacokinetics of EE 2 were distinctly nonlinear with substantial increases in the elimination half-life with increasing dose. The plasma concentration–time profiles of EE 2 were influenced by enterohepatic recirculation that caused multiple or secondary peaks in the profiles. In a separate experiment, the pharmacokinetics of purified VTG was characterized after intra-arterial injection in trout. After direct injection of VTG, plasma levels declined tri-exponentially with an apparent steady-state volume of distribution of 837 ml/kg; total body clearance was 31.1 ml/h per kg, and the elimination half-life was 43.7 h.

Defining and modeling known adverse outcome pathways: Domoic acid and neuronal signaling as a case study

An adverse outcome pathway (AOP) is a sequence of key events from a molecular-level initiating event and an ensuing cascade of steps to an adverse outcome with population-level significance. To implement a predictive strategy for ecotoxicology, the multiscale nature of an AOP requires computational models to link salient processes (e.g., in chemical uptake, toxicokinetics, toxicodynamics, and population dynamics). A case study with domoic acid was used to demonstrate strategies and enable generic recommendations for developing computational models in an effort to move toward a toxicity testing paradigm focused on toxicity pathway perturbations applicable to ecological risk assessment. Domoic acid, an algal toxin with adverse effects on both wildlife and humans, is a potent agonist for kainate receptors (ionotropic glutamate receptors whose activation leads to the influx of Na(+) and Ca²(+)). Increased Ca²(+) concentrations result in neuronal excitotoxicity and cell death, primarily in the hippocampus, which produces seizures, impairs learning and memory, and alters behavior in some species. Altered neuronal Ca²(+) is a key process in domoic acid toxicity, which can be evaluated in vitro. Furthermore, results of these assays would be amenable to mechanistic modeling for identifying domoic acid concentrations and Ca²(+) perturbations that are normal, adaptive, or clearly toxic. In vitro assays with outputs amenable to measurement in exposed populations can link in vitro to in vivo conditions, and toxicokinetic information will aid in linking in vitro results to the individual organism. Development of an AOP required an iterative process with three important outcomes: a critically reviewed, stressor-specific AOP; identification of key processes suitable for evaluation with in vitro assays; and strategies for model development.

The state of in vitro science for use in bioaccumulation assessments for fish

Through the concerted evaluations of thousands of commercial substances for the qualities of persistence, bioaccumulation, and toxicity as a result of the United Nations Environment Programs Stockholm Convention, it has become apparent that fewer empirical data are available on bioaccumulation than other endpoints and that bioaccumulation models were not designed to accommodate all chemical classes. Due to the number of chemicals that may require further assessment, in vivo testing is cost prohibitive and discouraged due to the large number of animals needed. Although in vitro systems are less developed and characterized for fish, multiple high-throughput in vitro assays have been used to explore the dietary uptake and elimination of pharmaceuticals and other xenobiotics by mammals. While similar processes determine bioaccumulation in mammalian species, a review of methods to measure chemical bioavailability in fish screening systems, such as chemical biotransformation or metabolism in tissue slices, perfused tissues, fish embryos, primary and immortalized cell lines, and subcellular fractions, suggest quantitative and qualitative differences between fish and mammals exist. Using in vitro data in assessments for whole organisms or populations requires certain considerations and assumptions to scale data from a test tube to a fish, and across fish species. Also, different models may incorporate the predominant site of metabolism, such as the liver, and significant presystemic metabolism by the gill or gastrointestinal system to help accurately convert in vitro data into representative whole-animal metabolism and subsequent bioaccumulation potential. The development of animal alternative tests for fish bioaccumulation assessment is framed in the context of in vitro data requirements for regulatory assessments in Europe and Canada.

DYNAMICS OF 17α-ETHYNYLESTRADIOL EXPOSURE IN RAINBOW TROUT (ONCORHYNCHUS MYKISS): ABSORPTION, TISSUE DISTRIBUTION, AND HEPATIC GENE EXPRESSION PATTERN

17alpha-Ethynylestradiol (EE2) is a synthetic estrogen identified in sewage effluents. To understand better the absorption kinetics of EE2 and the induction of vitellogenin (VTG) and estrogen receptor alpha (ERalpha) mRNA, we subjected male rainbow trout (Onchorynchus mykiss) to continuous water exposures of 125 ng/L of EE2 for up to 61 d. Trout were either repetitively sampled for blood plasma or serially killed at selected time intervals. Vitellogenin, ERalpha mRNA, and EE2 were measured using enzyme-linked immunosorbent assay and using quantitative polymerase chain reaction and gas chromatography-mass spectrometry, respectively. In separate experiments, trout were exposed to EE2 for 7 d, and hepatic gene expression was assessed using a low- and high-density cDNA microarray. The EE2 was rapidly absorbed by the trout, with an apparent equilibrium at 16 h in plasma and liver. The ERalpha mRNA levels also increased rapidly, reaching near-peak levels by 48 h. In contrast, plasma levels of VTG continuously increased for 19 d. After 61 d, tissues with the highest levels of VTG were the liver, kidney, and testes. Microarray-based gene expression studies provided unexpected results. In some cases, known estrogen-responsive genes (e.g., ERalpha) were unresponsive, whereas many of the genes that have no apparent link to estrogen function or EE2 toxicity were significantly altered in expression. Of the two microarray approaches tested in the present study, the high-density array appeared to be superior because of the improved quality of the hybridization signal and the robustness of the response in terms of the number of genes identified as being EE2 responsive.

Estrogen receptor mRNA expression patterns in the liver and ovary of female rainbow trout over a complete reproductive cycle.

Estrogens are critical hormones involved in reproduction and need to bind to estrogen receptors in target organs for biological activity. Fishes have two distinct estrogen receptor subtypes, alpha (α) and beta (β), with variable combinations of additional isoforms of each subtype dependent on the history of genome duplication within a taxon. The comparative expression patterns of estrogen receptor isoforms during the female reproductive cycle will provide important insights into the unique function and importance of each. The purpose of this study was to measure the mRNAs for the four estrogen receptor isoforms (erα1, erα2, erβ1, erβ2) in the liver and ovary of adult, female rainbow trout over the course of an annual reproductive cycle. The expression of estrogen receptor mRNA isoforms was measured by quantitative real-time RT-PCR. Several reproductive indices (gonadosomatic index, maximum oocyte diameter, plasma estradiol-17β, plasma vitellogenin, and ovulation) were also quantified for comparison and used in a correlation analysis to examine any inter-relationships. Of the four isoforms, the expression of erα1 was highest in the liver, and had a significant positive correlation with liver erβ1 expression. Liver expression of erα2 mRNA was the lowest, but showed a significant positive correlation with maximum oocyte diameter in the ovary. The pattern of the erβ isoforms in liver was one of initially elevated mRNA expression followed by a gradual decrease as reproductive development proceeded. In the ovary the erβ1 isoform had the highest mRNA expression of all estrogen receptor isoforms, at the beginning of the reproductive cycle, but then decreased afterward. Both ovarian erβ isoforms had a significant positive correlation with one another. In contrast, erα2 mRNA expression showed a high maximum level in the ovary near the end of the cycle along with a significant positive correlation with plasma estradiol-17β levels; the highest gonadosomatic indices, maximum oocyte diameter, and vitellogenin levels occurred then too.

Dichloroacetate toxicokinetics and disruption of tyrosine catabolism in B6C3F1 mice: dose–response relationships and age as a modifying factor

Dichloroacetate (DCA) is a rodent carcinogen commonly found in municipal drinking water supplies. Toxicokinetic studies have established that elimination of DCA is controlled by liver metabolism, which occurs by the cytosolic enzyme glutathione-S-transferase-zeta (GST-zeta). DCA is also a mechanism based inhibitor of GST-zeta, and a loss in GST-zeta enzyme activity occurs following repeated doses or prolonged drinking water exposures. GST-zeta is identical to an enzyme that is part of the tyrosine catabolism pathway known as maleylacetoacetate isomerase (MAAI). In this pathway, GST-zeta plays a critical role in catalyzing the isomerization of maleylacetoacetate to fumarylacetoacetate. Disruption of tyrosine catabolism has been linked to increased cancer risk in humans. We studied the elimination of i.v. doses of DCA to young (10 week) and aged (60 week) mice previously treated with DCA in their drinking water for 2 and 56 weeks, respectively. The diurnal change in blood concentrations of DCA was also monitored in mice exposed to three different drinking water concentrations of DCA (2.0, 0.5 and 0.05 g/l). Additional experiments measured the in vitro metabolism of DCA in liver homogenates prepared from treated mice given various recovery times following treatment. The MAAI activity was also measured in liver cytosol obtained from treated mice. Results indicated young mice were the most sensitive to changes in DCA elimination after drinking water treatment. The in vitro metabolism of DCA was decreased at all treatment rates. Partial restoration ( approximately 65% of controls) of DCA elimination capacity and hepatic GST-zeta activity occurred after 48 h recovery from 14 d 2.0 g/l DCA drinking water treatments. Recovery from treatments could be blocked by interruption of protein synthesis with actinomycin D. MAAI activity was reduced over 80% in liver cytosol from 10-week-old mice. However, MAAI was unaffected in 60-week-old mice. These results indicate that in young mice, inactivation and re-synthesis of GST-zeta is a highly dynamic process and that exogenous factors that deplete or reduce GST-zeta levels will decrease DCA elimination and may increase the carcinogenic potency of DCA. As mice age, the elimination capacity for DCA is less affected by reduced liver metabolism and mice appear to develop some toxicokinetic adaptation(s) to allow elimination of DCA at rates comparable to naive animals. Reduced MAAI activity alone is unlikely to be the carcinogenic mode of action for DCA and may in fact, only be important during the early stages of DCA exposure.

Intracellular, not membrane, estrogen receptors control vitellogenin synthesis in the rainbow trout.

The synthesis of vitellogenin, via estrogens, by the liver of female oviparous vertebrates provides the precursor for yolk proteins in developing oocytes. There are two distinct estrogenic transduction pathways in vertebrates that could control vitellogenin synthesis. One provides direct genomic (i.e., nuclear) control in which estrogens bind to estrogen receptors (ERs) that function as transcription factors within the cell nucleus. The other involves a non-genomic pathway initiated by estrogens binding to membrane-bound ERs at the cell surface. The objective of this paper was to determine which ER transduction pathway regulates hepatic vitellogenin synthesis in rainbow trout. For this study an estrogenic molecule, 17alpha-ethynylestradiol (EE2), was conjugated to a peptide moiety (PEP) to make 17alpha-ethynylestradiol-peptide (EE2-PEP) to bind to membrane-bound ERs. This was compared with EE2 that is capable of crossing the cell membrane and binding to intracellular ERs. An in vivo experiment using male rainbow trout injected with either EE2-PEP or EE2 demonstrated that only EE2 stimulated a significant increase in plasma vitellogenin concentrations. This was further confirmed by treating male rainbow trout hepatocytes in primary culture for 24h with PEP, EE2-PEP or EE2. Only the EE2 treatment resulted in significantly higher vitellogenin expression in trout hepatocytes. These results demonstrate that estrogens must gain entry into hepatocytes to bind to intracellular ERs in order to stimulate vitellogenin synthesis. While this study cannot conclude that a membrane ER system is absent in the rainbow trout liver, it has established that the liver synthesis of vitellogenin in rainbow trout is regulated by intracellular ERs.

Sex differences in the uptake and disposition of perfluorooctanoic acid in fathead minnows after oral dosing.

Perfluorooctanoic acid (PFOA) among other perfluorinated acids is becoming recognized as a ubiquitous environmental contaminant. PFOA is resistant to environmental degradation and appears to undergo no biotransformation in animals. Previous toxicokinetic studies in rodents have indicated that urinary excretion is the most important elimination pathway once PFOA has been absorbed. In some species such as rats, large sex-related differences in urinary excretion have been reported, with females having a much shorter blood or plasma elimination half-life than that of males. It is unknown whether this phenomenon occurs in fish. Therefore, this study determined the disposition of PFOA in male and female fathead minnows (Pimephales promelas) after a single oral dose of PFOA. After dosing, minnows were subsequently euthanized at various times until 336 h postdosing and the PFOA concentration was measured in plasma, gonads, and fish carcass. The concentration-time profiles of PFOA were then analyzed using toxicokinetic methods. The results indicated a clear sex difference in the elimination of PFOA. The plasma elimination half-life of PFOA in female minnows was 6.3 h while in male minnows it was 68.5 h. Pretreatment of female minnows with the synthetic androgen trenbolone substantially delayed the elimination of PFOA, causing the elimination half-life to increase to 25.3 h. In males, pretreatment with the synthetic estrogen ethynylestradiol (EE2) had little effect on PFOA toxicokinetics. These results indicate that the sex differences in PFOA elimination in fathead minnows can at least partially be modulated by exposure to synthetic sex steroids. Whether sex differences in PFOA elimination in minnows is attributable to differences in renal transport activity, as it appears to be for rodents, is unknown at present but clearly warrants further study.

Use of In Vitro Absorption, Distribution, Metabolism, and Excretion (ADME) Data in Bioaccumulation Assessments for Fish

ABSTRACT A scientific workshop was held in 2006 to discuss the use of in vitro Absorption, Distribution, Metabolism, and Excretion (ADME) data in chemical bioaccumulation assessments for fish. Computer-based (in silico) modeling tools are widely used to estimate chemical bioaccumulation. These in silico methods have inherent limitations that result in inaccurate estimates for many compounds. Based on a review of the science, workshop participants concluded that two factors, absorption and metabolism, represent the greatest sources of uncertainty in current bioaccumulation models. Both factors can be investigated experimentally using in vitro test systems. A variety of abiotic and biotic systems have been used to predict chemical accumulation by invertebrates, and dietary absorption of drugs and xenobiotics by mammals. Research is needed to determine whether these or similar methods can be used to better predict chemical absorption across the gills and gut of fish. Scientists studying mammals have developed a stepwise approach to extrapolate in vitro hepatic metabolism data to the whole animal. A series of demonstration projects was proposed to investigate the utility of these in vitro–in vivo extrapolation procedures in bioaccumulation assessments for fish and delineate the applicability domain of different in vitro test systems. Anticipating research progress on these topics, participants developed a “decision tree” to show how in vitro information for individual compounds could be used in a tiered approach to improve bioaccumulation assessments for fish and inform the possible need for whole-animal testing.