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Interaction of environmental estrogens with the estrogen receptor (ER) has been shown in various fish species. Our objective was to compare the sensitivity of bream (Abramis brama) to (xeno-)estrogens with that of the carp (Cyprinus carpio), by measuring the effects of 17beta-estradiol (E2), estrone (E1), ethynylestradiol (EE2), bisphenol A (BPA), nonylphenol (NP), methoxychlor (MXCL), and halogenated aromatic hydrocarbons (HAHs) such as polychlorinated biphenyls (PCB126, PCB118), 2,3,7,8-tetrachlorodibenzo-dioxin (TCDD), and 2,3,4,7,8-pentachlorodibenzofuran (PCDF) on vitellogenesis in primary hepatocytes. Comparing the EC50 values in bream hepatocytes: EE2 (0.1-0.2 microM) < E1 (0.6-0.2 microM) < E2 (1.9 microM) with those of carp hepatocytes EE2 (0.03-0.06 microM) < E2 (0.3 microM) approximately E1 (0.2-0.3 microM) we found differences in sensitivity and ranking of the estrogenic potency of E2 and E1, indicating interspecies differences. Exposure to BPA, NP, MXCL, and HAHs did not or only weakly induce vitellogenesis. Bream hepatocytes coexposed to E2 and TCDD, PCB126 or PCDF showed a concentration-dependent inhibition of E2-induced vitellogenesis. IC50 (concentration of a compound that elicits 50% inhibition of E2-induced vitellogenesis) values determined in bream were: TCDD (0.02-0.09 nM) < PCB126 (0.35-0.1 nM) < PCDF (2.0-0.1) and in carp were: TCDD (0.01 nM) < PCB126 (0.4 nM). PCB118 showed no (anti-)estrogenic response. IC50 values and benchmark-concentration for TCDD and PCB126 in bream and carp hepatocytes were in the same range, indicating similar sensitivity to these compounds. Due to their anti-estrogenic capacity with benchmark-concentrations in the pM range TCDD, PCDF, and PCB126 may form a potential hazard for the reproductive success of fish species by inhibition of vitellogenesis.

Vitellogenin (vtg) is a precursor of the yolk proteins lipovitelline and phosvitin and is synthesized as a consequence of estrogen-dependent gene expression in female and male hepatocytes of egg-laying vertebrates. Freshly isolated carp hepatocytes of a genetically uniform strain of adult male carp (Cyprinus carpio) were used to investigate the effects of primary exposure to estrogenic compounds on the vitellogenic response to xenoestrogens. Isolated carp hepatocytes were first exposed (primary exposure) to 50 or 100 microM of either methoxychlor (MXCL) or bisphenol A (BPA), different concentrations of estrone (E1; 1 or 10 nM) or 17beta-estradiol (E2; 0.1 or 1 nM) for 2 days. Hepatocytes were exposed to xenoestrogens (secondary exposure) at both 2 and 5 days after isolation. Hepatocytes were cultured for a total period of 8 days. A competitive indirect ELISA was used to determine the level of vtg after 8 days. The concentration of chemicals used for the primary exposure induced vtg to a level that was less than 10% of the response elicited by E2 (1000 nM). A cytotoxic response, measured by MTT, was not observed after primary exposure to any of the xenoestrogens. After primary exposure to MXCL, vtg production in response to E2 was increased by 4-fold, and vitellogenesis in response to E1 treatment was doubled compared with vitellogenesis without pretreatment. No significant differences were observed between primary exposure to 50 and 100 microM MXCL. Primary exposure to 50 and 100 microM BPA increased the maximum vtg production in response to secondary E2 exposure by about 5- and 7-fold, respectively. Primary exposure to BPA (50 and 100 microM) followed by secondary exposure to E1 showed a 4- and 5-fold increase of the vtg synthesis in comparison to E1 exposure alone. Primary exposure to the endogenous estrogens had no significant influence on the vtg synthesis in response to secondary exposure to E1 or E2. Compared to hepatocytes exposed only to MXCL or BPA, primary exposure to E2 increased the vtg synthesis in hepatocytes induced by MXCL or BPA by almost a factor of 2. Primary exposure to E1 increased vitellogenesis after secondary exposure to MXCL only marginally. The present results indicate that weakly estrogenic environmental chemicals such as MXCL and BPA can increase the sensitivity of carp hepatocytes towards endogenous estrogens with respect to VTG synthesis.

A healthy immune status is strongly conditioned during early life stages. Insights into the molecular drivers of early life immune development and function are prerequisite to identify strategies to enhance immune health. Even though several starting points for targeted immune modulation have been identified and are being developed into prophylactic or therapeutic approaches, there is no regulatory guidance on how to assess the risk and benefit balance of such interventions. Six early life immune causal networks, each compromising a different time period in early life (the 1st, 2nd, 3rd trimester of gestations, birth, newborn, and infant period), were generated. Thereto information was extracted and structured from early life literature using the automated text mining and machine learning tool: Integrated Network and Dynamical Reasoning Assembler (INDRA). The tool identified relevant entities (e.g., genes/proteins/metabolites/processes/diseases), extracted causal relationships among these entities, and assembled them into early life-immune causal networks. These causal early life immune networks were denoised using GeneMania, enriched with data from the gene-disease association database DisGeNET and Gene Ontology resource tools (GO/GO-SLIM), inferred missing relationships and added expert knowledge to generate information-dense early life immune networks. Analysis of the six early life immune networks by PageRank, not only confirmed the central role of the "commonly used immune markers" (e.g., chemokines, interleukins, IFN, TNF, TGFB, and other immune activation regulators (e.g., CD55, FOXP3, GATA3, CD79A, C4BPA), but also identified less obvious candidates (e.g., CYP1A2, FOXK2, NELFCD, RENBP). Comparison of the different early life periods resulted in the prediction of 11 key early life genes overlapping all early life periods (TNF,