Genome-wide scan reveals signatures of selection related to pollution adaptation in non-model estuarine Atlantic killifish (Fundulus heteroclitus).

In many human-altered ecosystems, organisms are increasingly faced with more diverse and complex environmental stressors and pollutant mixtures, to which the adaptations necessary to survive exposure are likely to be numerous and varied. Improving our understanding of the molecular mechanisms that underlie complex polygenic adaptations in natural settings requires significant toxicological, biochemical, physiological, and genomic data rarely available for non-model organisms. Here, we build upon two decades of study of adaptation to anthropogenic pollutants in a population of Atlantic killifish (Fundulus heteroclitus) that inhabits the creosote-contaminated Atlantic Wood Industries Superfund (AW) site on the Elizabeth River, Virginia in the United States. To better understand the genotypes that underlie previously characterized resistance to PCBs and PAHs, we performed Restriction site-Associated DNA sequencing (RADseq) on killifish from AW and two relatively clean reference sites (King's Creek-KC, and Mains Creek-MC). Across the genome, we analyzed over 83,000 loci and 12,000 single nucleotide polymorphisms (SNPs). Shared across both comparisons of killifish from polluted (AW) and relatively unpolluted (KC and MC) sites, we found eight genomic regions with smoothed FST values significantly (p < 0.001) elevated above background. Using the recently published F. heteroclitus reference genome, we identified candidate genes in these significant regions involved in the AHR pathway (e.g. AIP, ARNT1c), as well as genes relating to cardiac structure and function. These genes represent both previously characterized and potentially novel molecular adaptations involved with various aspects of resistance to these environmental toxins.

Resistance to polycyclic aromatic hydrocarbon toxicity and associated bioenergetic consequences in a population of Fundulus heteroclitus.

Several locations in the Elizabeth River, VA, USA are highly contaminated with polycyclic aromatic hydrocarbons (PAHs) due to the release of creosote mixtures from wood treatment facilities. Interestingly, some populations of Atlantic killifish (Fundulus heteroclitus) inhabiting the Elizabeth River (ER) are resistant to PAH-induced teratogenesis. However, evolutionary resistance to PAHs due to chronic PAH exposure is associated with reduced fitness and increased susceptibility to other environmental stressors in at least one PAH-resistant ER killifish population. More specifically, wild-caught and first generation PAH-resistant juvenile killifish have altered metabolic demands when compared to non-resistant fish. Herein, we investigated this association further by examining a previously under-studied population captured from the creosote-contaminated site Republic Creosoting (Rep). We assessed PAH toxicity and effects on energy metabolism in Rep killifish in comparison with killifish from the reference site Kings Creek (KC). Following exposures to simple and complex PAH mixtures, Rep killifish exhibited several phenotypes associated with PAH resistance including decreased incidences of developmental cardiovascular deformities and recalcitrant cytochrome P450 1A (CYP1A) activity. We evaluated bioenergetics in killifish embryos throughout development and found elevated basal oxygen consumption rates in Rep embryos relative to KC embryos. Furthermore, juvenile F1 Rep fish had significantly lower maximal metabolic rates and aerobic scopes than KC juveniles. These results suggest that populations of killifish that have adapted or evolved to withstand the toxicity associated with PAHs consequently have altered energetic metabolism or demands. Such consequences could result in an enhanced vulnerability to other environmental and anthropogenic stressors in PAH-resistant killifish.

Embryonic cardiotoxicity of weak aryl hydrocarbon receptor agonists and CYP1A inhibitor fluoranthene in the Atlantic killifish (Fundulus heteroclitus).

High affinity aryl hydrocarbon receptor (AHR) ligands, such as certain polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), cause severe cardiac teratogenesis in fish embryos. Moderately strong AHR agonists, for example benzo[a]pyrene and ß-naphthoflavone, are capable of causing similar cardiotoxic effects, particularly when coupled with cytochrome P450 1A (CYP1A) inhibitors (e.g., fluoranthene (FL). Additionally, some weaker AHR agonists (carbaryl, 2-methylindole, 3-methylindole, and phenanthrene) are known to also cause cardiotoxicity in zebrafish (Danio rerio) embryos when coupled with FL; however, the cardiotoxic effects were not mediated specifically by AHR stimulation. This study was performed to determine if binary exposure to weak AHR agonists and FL were also capable of causing cardiotoxicity in Atlantic killifish Fundulus heteroclitus embryos. Binary exposures were performed in both naïve and PAH-adapted killifish embryos to examine resistance to weak agonists and FL binary exposures. Weak agonists used in this study included the following: carbaryl, phenanthrene, 2-methylindole, 3-methylindole, indigo, and indirubin. Carbaryl, indigo, and indirubin induced the highest CYP1 activity levels in naïve killifish embryos, but no significant CYP1 induction was observed in the PAH-adapted killifish. Embryos were coexposed to subteratogenic levels of each agonist and 500µg/L FL to assess if binary administration could cause cardiotoxicity. Indigo and indirubin coupled with FL caused cardiac teratogenesis in naïve killifish, but coexposures did not produce cardiac chamber abnormalities in the PAH-adapted population. Knockdown of AHR2 in naïve killifish embryos did not prevent cardiac teratogenesis. The data suggest a unique mechanism of cardiotoxicity that is not driven by AHR2 activation.

Antioxidant Rescue of Selenomethionine-Induced Teratogenesis in Zebrafish Embryos.

Selenium (Se) is an essential micronutrient that can be found at toxic concentrations in surface waters contaminated by runoff from agriculture and coal mining. Zebrafish (Danio rerio) embryos were exposed to aqueous Se in the form of selenate, selenite, and l-selenomethionine (SeMet) in an attempt to determine if oxidative stress plays a role in selenium embryo toxicity. Selenate and selenite exposure did not induce embryo deformities (lordosis and craniofacial malformation). l-selenomethionine, however, induced significantly higher deformity rates at 100 µg/L compared with controls. SeMet exposure induced a dose-dependent increase in the catalytic subunit of glutamate-cysteine ligase (gclc) and reached an 11.7-fold increase at 100 µg/L. SeMet exposure also reduced concentrations of TGSH, RGSH, and the TGSH:GSSG ratio. Pretreatment with 100 µM N-acetylcysteine significantly reduced deformities in the zebrafish embryos secondarily treated with 400 µg/L SeMet from approximately 50­10 % as well as rescued all three of the significant glutathione level differences seen with SeMet alone. Selenite exposure induced a 6.6-fold increase in expression of the glutathione-S-transferase pi class 2 (gstp2) gene, which is involved in xenobiotic transformation and possibly oxidative stress. These results suggest that aqueous exposure to SeMet can induce significant embryonic teratogenesis in zebrafish that are at least partially attributed to oxidative stress.

Developmental exposure to a complex PAH mixture causes persistent behavioral effects in naive Fundulus heteroclitus (killifish) but not in a population of PAH-adapted killifish.

Acute exposures to some individual polycyclic aromatic hydrocarbons (PAHs) and complex PAH mixtures are known to cause cardiac malformations and edema in the developing fish embryo. However, the heart is not the only organ impacted by developmental PAH exposure. The developing brain is also affected, resulting in lasting behavioral dysfunction. While acute exposures to some PAHs are teratogenically lethal in fish, little is known about the later life consequences of early life, lower dose subteratogenic PAH exposures. We sought to determine and characterize the long-term behavioral consequences of subteratogenic developmental PAH mixture exposure in both naive killifish and PAH-adapted killifish using sediment pore water derived from the Atlantic Wood Industries Superfund Site. Killifish offspring were embryonically treated with two low-level PAH mixture dilutions of Elizabeth River sediment extract (ERSE) (TPAH 5.04 µg/L and 50.4 µg/L) at 24h post fertilization. Following exposure, killifish were raised to larval, juvenile, and adult life stages and subjected to a series of behavioral tests including: a locomotor activity test (4 days post-hatch), a sensorimotor response tap/habituation test (3 months post hatch), and a novel tank diving and exploration test (3months post hatch). Killifish were also monitored for survival at 1, 2, and 5 months over 5-month rearing period. Developmental PAH exposure caused short-term as well as persistent behavioral impairments in naive killifish. In contrast, the PAH-adapted killifish did not show behavioral alterations following PAH exposure. PAH mixture exposure caused increased mortality in reference killifish over time; yet, the PAH-adapted killifish, while demonstrating long-term rearing mortality, had no significant changes in mortality associated with ERSE exposure. This study demonstrated that early embryonic exposure to PAH-contaminated sediment pore water caused long-term locomotor and behavioral alterations in killifish, and that locomotor alterations could be observed in early larval stages. Additionally, our study highlights the resistance to behavioral alterations caused by low-level PAH mixture exposure in the adapted killifish population. Furthermore, this is the first longitudinal behavioral study to use killifish, an environmentally important estuarine teleost fish, and this testing framework can be used for future contaminant assessment.

Bioaccumulation and speciation of selenium in fish and insects collected from a mountaintop removal coal mining-impacted stream in West Virginia.

A major contaminant of concern for mountaintop removal/valley fill (MTR/VF) coal mining is selenium (Se), an essential micronutrient that can be toxic to fish. Creek chubs (Semotilus atromaculatus), green sunfish (Lepomis cyanellus), and composite insect samples were collected in March-July, 2011-2013 at two sites within the Mud River, West Virginia. One site (MR7) receives MTR/VF coal mining effluent, while the reference site (LFMR) does not. MR7 water had significantly higher concentrations of soluble Se (p < 0.01) and conductivity (p < 0.005) compared to LFMR. MR7 whole insects contained significantly higher concentrations of Se compared to LFMR insects (p < 0.001). MR7 creek chubs had significantly higher Se in fillets, liver, and ovary tissues compared to LFMR samples (p < 0.0001, p < 0.0001, and p < 0.02, respectively). MR7 green sunfish fillets contained significantly higher Se (p < 0.0001). Histological examination showed LFMR creek chub gills contained a typical amount of parasitic infestations; however MR7 gills contained minimal to no visible parasites. X-ray absorption spectroscopic analyses revealed that MR7 whole insects and creek chub tissues primarily contained organic Se and selenite. These two species of Mud River fish were shown to specifically accumulate Se differently in tissues compartments. Tissue-specific concentrations of Se may be useful in determining potential reproductive consequences of Se exposure in wild fish populations.

Resistance to teratogenesis by F1 and F2 embryos of PAH-adapted Fundulus heteroclitus is strongly inherited despite reduced recalcitrance of the AHR pathway.

Atlantic killifish (Fundulus heteroclitus) inhabiting the Atlantic Wood Superfund site on the Elizabeth River (Portsmouth, VA, USA) are exposed to a complex mixture of polycyclic aromatic hydrocarbons (PAHs) from former creosote operations, but are resistant to the acute toxicity and cardiac teratogenesis caused by PAHs. The resistance is associated with a dramatic recalcitrance to induction of cytochrome P450 (CYP1) metabolism enzymes following exposure to aryl hydrocarbon receptor (AHR) agonists, along with an elevated antioxidant response and increased expression of several other xenobiotic metabolism and excretion enzymes. However, the heritability of the resistance in the absence of chemical stressors has been inconsistently demonstrated. Understanding the heritability of this resistance will help clarify the nature of population-level responses to chronic exposure to PAH mixtures and aid in identifying the important mechanistic components of resistance to aryl hydrocarbons. We compared the response of Atlantic Wood F1 and F2 embryos to benzo[k]fluoranthene (BkF), benzo[a]pyrene (BaP), 3,3',4,4',5-pentachlorobiphenyl (PCB-126), and a mixture of BkF and fluoranthene (Fl) to that of F1 embryos of reference site killifish. Resistance to cardiac teratogenesis and induction of CYP mRNA expression and CYP activity was determined. We found that both Atlantic Wood F1 and F2 embryos were highly resistance to cardiac teratogenesis. However, the resistance by Atlantic Wood F2 embryos to induction of CYP mRNA expression and enzyme activity was intermediate between that of Atlantic Wood F1 embryos and reference embryos. These results suggest that resistance to cardiac teratogenesis in Atlantic Wood fish is conferred by multiple factors, not all of which appear to be fully genetically heritable.

Cerium oxide nanoparticles are more toxic than equimolar bulk cerium oxide in Caenorhabditis elegans.

Engineered cerium oxide nanoparticles (CeO2 NPs) are widely used in biomedical and engineering manufacturing industries. Previous research has shown the ability of CeO2 NPs to act as a redox catalyst, suggesting potential to both induce and alleviate oxidative stress in organisms. In this study, Caenorhabditis elegans and zebrafish (Danio rerio) were dosed with commercially available CeO2 NPs. Non-nano cerium oxide powder (CeO2) was used as a positive control for cerium toxicity. CeO2 NPs suspended in standard United States Environmental Protection Agency reconstituted moderately hard water, used to culture the C. elegans, quickly formed large polydisperse aggregates. Dosing solutions were renewed daily for 3 days. Exposure of wild-type nematodes resulted in dose-dependent growth inhibition detected for all 3 days (p < 0.0001). Non-nano CeO2 also caused significant growth inhibition (p < 0.0001), but the scale of inhibition was less at equivalent mass exposures compared with CeO2 NP exposure. Some metal and oxidative stress-sensitive mutant nematode strains showed mildly altered growth relative to the wild-type when dosed with 5 mg/L CeO2 NPs on days 2 and 3, thus providing weak evidence for a role for oxidative stress or metal sensitivity in CeO2 NP toxicity. Zebrafish microinjected with CeO2 NPs or CeO2 did not exhibit increased gross developmental defects compared with controls. Hyperspectral imaging showed that CeO2 NPs were ingested but not detectable inside the cells of C. elegans. Growth inhibition observed in C. elegans may be explained at least in part by a non-specific inhibition of feeding caused by CeO2 NPs aggregating around bacterial food and/or inside the gut tract.

Accumulation of environmental contaminants in wood duck (Aix sponsa) eggs, with emphasis on polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans.

We measured polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), polychlorinated biphenyls (PCBs), organochlorine pesticides, and mercury in wood duck (Aix sponsa) eggs collected near a North Carolina (USA) bleached kraft paper mill. Samples were taken a decade after the mill stopped using molecular chlorine. Using avian toxic equivalency factors, 2,3,7,8-tetrachlorodibenzo-p-dioxin toxicity equivalent (TEQ) concentrations were 1-30 pg/g fresh wet weight in eggs (n = 48) collected near the mill in 2002-2005 and were significantly higher than those from a reference site (<1 pg/g) 25 km away. Geometric mean wood duck egg TEQs (6 pg/g) were one-fifth those measured at this site prior to the cessation of molecular chlorine bleaching. Concentrations of mercury in wood duck eggs from nests of the Roanoke River sites ranged from 0.01 to 0.14 microg/g (geometric mean, 0.04 microg/g) and were significantly higher than those from the reference site, where concentrations did not exceed 0.04 microg/g (geometric mean, 0.02 mug/g). All concentrations were lower than those associated with adverse effects in birds. The congener profiles, lack of contamination in reference site eggs, and decline in contaminant concentrations after process changes at the mill provide strong evidence that mill discharges influenced contamination of local wood duck eggs. Collectively, the results indicate that the wood duck is an effective sentinel of the spatial and temporal extent of PCDD, PCDF, and mercury contamination.

Embryo toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin to the wood duck (Aix sponsa).

We examined the sensitivity of the wood duck (Aix sponsa) embryo to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) by injecting the toxicant into their eggs. Six groups of wood duck eggs (n = 35 to 211 per trial) were injected with 0 to 4600 pg TCDD/g egg between 2003 and 2005. Injections were made into yolk prior to incubation, and eggs were subsequently incubated and assessed weekly for mortality. Significant TCDD-induced mortality was not observed through day 25 (90% of incubation). Liver, heart, eye, and brain histology were generally unremarkable. Hepatic ethoxyresorufin-O-deethylase activity, a biomarker of dioxin-like compound exposure, was induced by 12-fold in the 4600 pg/g treatment relative to controls. The median lethal dose for chicken (Gallus domesticus) eggs we dosed identically to wood duck eggs was about 100 pg/g, similar to other assessments of chickens. Among dioxin-like compound embryo lethality data for 15 avian genera, the wood duck 4600 pg/g no-observed-effect level ranks near the middle. Because no higher doses were tested, wood ducks may be like other waterfowl (order Anseriformes), which are comparatively tolerant to embryo mortality from polychlorinated dibenzo-p-dioxins and dibenzofurans when exposed by egg injection.

Lack of p53 induction in fish cells by model chemotherapeutics.

Although p53 has been extensively studied in mammalian models, relatively little is known about its specific function in lower vertebrates. It has long been assumed that p53 pathways characterized in mammals apply to other vertebrates as well. Fish provide a useful model for the study of environmental carcinogenesis, and populations of fish inhabiting highly polluted environments provide information on the etiology of pollutant-mediated cancer. In this study, we investigated p53 protein and apoptosis induction in PLHC-1 (desert topminnow hepatocellular carcinoma), RTL-W1 (rainbow trout normal liver), and primary rainbow trout hepatocytes exposed to model chemotherapeutics. All of the chemicals used in these studies have been demonstrated to increase p53 protein levels and induce apoptosis in mammalian cell lines. In contrast, PLHC-1 p53 protein was not induced in response to any model mammalian p53 inducers following 24 h exposures. Additionally, both trout cell types demonstrated this same lack of p53 induction upon exposure to model chemotherapeutic drugs. PLHC-1 cells demonstrated an induction of apoptosis as measured by caspase-3 activation following exposure to all of the chemotherapeutics tested. Our results suggest that fish p53 may be activated differently from that of their mammalian counterparts, and that important differences may exist between phyla in the function and regulation of p53 as well as other mechanisms involved in environmental carcinogenesis.

In vivo and in vitro inhibition of CYP1A-dependent activity in Fundulus heteroclitus by the polynuclear aromatic hydrocarbon fluoranthene.

Certainpolynuclear aromatic hydrocarbons (PAHs) such as benzo[a]pyrene (BaP) induce CYP1A-dependent enzyme activities. Because PAHs are ubiquitous environmental contaminants, and some are aryl hydrocarbon agonists, CYP1A has been used as a biomarker for PAH exposure. However, PAHs exist in the environment in complex mixtures that may confound biomarker results. In in vitro studies, the PAH fluoranthene (FL) failed to increase or enhance CYP1A1-dependent ethoxyresorufin-O-deethylase (EROD) activity in cells, but rather inhibited activities induced by AhR agonists such as 2,3,7,8-tetrachlorodibenzo-p-dioxin and benzo(k)fluoranthene. In order to determine the in vivo effects of FL on CYP1A and DNA adduct levels, Fundulus heteroclitus were given single ip injections of either BaP (5 mg/kg), BaP + FL (5 mg/kg each), BaP + FL (5 and 50 mg/kg, respectively), FL (5 mg/kg), FL (50 mg/kg), or corn oil control. BaP-treated fish had liver microsome EROD activities significantly higher than controls, whereas FL-treated fish were not different from controls. EROD activities in BaP + FL cotreatments were significantly lower compared to fish treated with BaP alone. When FL was incubated with BaP-induced microsomes, the IC50 for inhibition of EROD activity was 1.4 x 10(-5) M FL. Kinetic studies indicated a significant noncompetitive component to the FL inhibition. When fish were treated with [(14)C]FL, the concentration of radiolabel associated with microsomal preparations was four orders of magnitude lower than the IC50. Therefore, the presence of FL or a FL metabolite was insufficient to account for the inhibition by a kinetic mechanism. In contrast to cell studies, CYP1A immunoreactive protein was significantly decreased in vivo by FL cotreatment, indicating that FL may inhibit EROD activity by down-regulating the CYP1A protein. A covalent interaction of [(14)C]FL with CYP1A was not detected. Total (32)P-postlabeled DNA adducts were not significantly changed by cotreatment of FL and BaP; however, cotreatment with 50 mg/kg FL decreased one adduct and increased another significantly. Because FL and perhaps other inhibitory PAHs, co-occur in the environment with CYP1A inducers, CYP1A-dependent bioassays may cause an underestimation of PAH exposures.

2,3,7,8-Tetrachlorodibenzo-p-dioxin induces apoptotic cell death and cytochrome P4501A expression in developing Fundulus heteroclitus embryos.

Fundulus heteroclitus embryos were exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) during early development using nanoinjection or water bath exposure. TCDD caused developmental abnormalities that included hemorrhaging, loss of vascular integrity, edema, stunted development and death. The LC(50) and LD(50) of TCDD for Fundulus embryos were approximately 19.7+/-9.5 pg TCDD/microl (water bath) and 0.25+/-0.09 ng TCDD/g embryo (nanoinjection). To identify a possible cause for these developmental abnormalities we analyzed the effects of TCDD on apoptotic cell death and cytochrome P4501A (CYP1A) expression in the embryos. TCDD exposure increased apoptotic cell death in several tissues including brain, eye, gill, kidney, tail, intestine, heart, and vascular tissue. CYP1A expression was also increased in the TCDD-exposed embryos predominantly in liver, kidney, gill, heart, intestine, and in vascular tissues throughout the embryo. There was co-occurrence of TCDD-induced apoptosis and CYP1A expression in some, but not all, cell types. In addition the dose response relationships for apoptosis and mortality were similar, while CYP1A expression appeared more sensitive to TCDD induction.

No detectable DNA excision repair in UV-exposed hepatocytes from two catfish species.

DNA repair is a critical process in protecting cellular genetic information from mutation. Nucleotide excision repair (NER) is a mechanism by which cells correct DNA damage caused by agents that form bulky covalent adducts and UV photoproducts such as thymine dimers and 6-4 photoproduct. NER, sometimes called dark repair, is generally accepted as being low in fish compared to mammals. This study was designed to quantitate NER in two related catfish species that have known differential sensitivities to liver carcinomas. The original hypothesis was that the more cancer resistant species, channel catfish (Ictalurus punctatus), would have more efficient DNA repair compared to the more sensitive brown bullhead (Ameriurus nebulosus). In order to measure NER, primary cultured hepatocytes of both species were exposed to UV light (10-40 J/m2) and collected at 0, 24, 48 and 72 h after exposure. Total DNA was extracted from the cells and incubated with T4 endonuclease V. Using alkaline gel electrophoresis, endonuclease sensitive sites (ESS) were quantified. Results from the ESS assay indicated there was a UV dose-response increase in thymine dimers from 0 to 40 J/m2. However, no repair (decrease in number of ESS) occurred in either fish species over a 72-h time period. When cells were exposed to photoreactivating fluorescent light, repair was detected. These studies highlight the difficulty of measuring NER in fish and are consistent with the low levels of NER reported by other researchers in fish.

Vitellogenin association and oocytic accumulation of thyroxine and 3, 5,3'-triiodothyronine in gravid Fundulus heteroclitus.

The association of the thyroid hormone (TH) thyroxine (T(4)) and its metabolically active metabolite 3,5,3'-triiodothyronine (T(3)) with serum vitellogenin (VTG) in gravid female and estrogenized male (E2+) Fundulus heteroclitus was investigated. In in vivo, time-course experiments, sera from gravid female fish exposed to [(125)I]T(4) showed time- and dose-dependent increases in total [(125)I]TH content. The [(125)I]T(4):[(125)I]T(3) ratio was also affected by dose and time. In analysis of sera from female fish, >80% of detected radioactivity was associated with VTG (approximately 35%) and a second chromatographic peak (approximately 45%), a lipoprotein fraction possibly consisting of high-density lipoproteins. In experiments comparing estrogenized versus control male fish, the presence of VTG significantly increased the overall quantity and altered the profile of serum protein-associated [(125)I]TH. When serum VTG was present in the very large quantities typical of male fish treated with high doses of E2, the majority (59-70%) of detected radioactivity was associated with VTG. Both [(125)I]T(4) and [(125)I]T(3) were detected in extracts from oocytes collected during the in vivo female study. The total TH content and [(125)I]T(4):[(125)I]T(3) ratios in these extracts presented an accumulation profile that mirrored, in a delayed manner, the profiles observed in sera data. Furthermore, this accumulation was related to oocyte maturational state (i.e., size) and, correspondingly, VTG uptake. Together, these data suggest an important role for VTG as a vector of maternal transfer for both T(4) and T(3).

Comparative metabolism and excretion of benzo(a)pyrene in 2 species of ictalurid catfish.

Differential susceptibility of polycyclic aromatic hydrocarbon (PAH)-mediated liver cancer exists in two related species of Ictalurid catfish. Two hypotheses are addressed in this study to explain this difference. Specifically, the relatively insensitive channel catfish 1) do not produce mutagenic PAH metabolites, and/or 2) they more quickly eliminate PAHs due to greater Phase II enzyme activities than the more sensitive brown bullhead. Livers and bile were collected from each species 6, 24, 72, and 168 h after a single 10 mg/kg i.p. benzo(a)pyrene (BaP) exposure. BaP treatment had no significant effect on cytosolic 1-chloro-2,4-dinitrobenzene or ethacrynic acid (EA)-glutathione-S:- transferase (GST) and cis-stilbene oxide-microsomal epoxide hydrolase (EH) activities of either species. Channel catfish EH and GST activities were 1.2-fold higher than brown bullhead activities (p = 0.058 and p < 0.002, respectively). HPLC-APCI-MS of extracted bile and bile enzymatically digested to detect glucuronyl transferase (GT), GST, and sulfotransferase (ST) conjugated metabolites indicated no species differences in elimination or profiles of total biliary metabolites. GT conjugates predominated; ST and GST conjugates were minimal. BaP-diones accounted for the majority of metabolites in both species. Overall, these results indicated that brown bullhead preferentially formed BaP-7,8-dihydrodiol, a precursor to the DNA-reactive BaP-7, 8-dihydrodiol-9,10-epoxide (BPDE), which may be linked to the increased PAH susceptibility in this species.

An enzyme-linked immunosorbent assay for estrogenicity using primary hepatocyte cultures from the channel catfish (Ictalurus punctatus).

An in vitro assay has been developed to screen for estrogenic activity of single chemicals or complex mixtures. This method combines primary hepatocyte cultures from the channel catfish (Ictalurus punctatus) with an enzyme-linked immunosorbant assay (ELISA) to detect and quantify the production of vitellogenin (VTG), a liver-derived, estrogen-induced lipoprotein. A variety of environmentally relevant chemicals and chemical mixtures were tested, including the polyaromatic hydrocarbon benzo(a)pyrene (BaP), the alkylphenolic surfactants 4-tert-octylphenol (OP) and p-nonylphenol (NP), the chlorinated insecticide o,p'-DDT, the plant derivative stigmastanol, and a number of waste waters from pulp and paper mills. In addition, the effects of estradiol (E2), the synthetic estrogen diethylstilbestrol (DES) and the antiestrogens trans-1-(4-beta-dimethylamino-ethoxyphenyl)-1,2-diphenylbut-1-ene (tamoxifen) and 7alpha-[9-(4,4,5,5, 5-pentafluoro-pentylsulfinyl)nonyl]estra-3,17beta-diol (ICI-182,780) were also examined. The following compounds were observed to be estrogenic: DES > E2 >> OP > o,p'-DDT > NP. Tests with BaP, stigmastanol, tamoxifen, ICI-182,780, and four paper mill effluents exhibited no detectable estrogenic activity. Furthermore, both tamoxifen and ICI-182,780 significantly reduced VTG synthesis by cells incubated with E2 or DES. Stigmastanol and the mill effluents were also tested for anti-estrogenic activity in cells incubated in media containing both DES and stigmastanol or effluent. Compared to DES alone, none of these treatments caused a significant reduction in the media concentrations of VTG. The detection limit for this assay was typically 15-25 ng VTG/ml medium. Screening results and performance characteristics such as inter- and intra-assay variability were similar to those reported for VTG assays for other teleost species. Thus, the present work provides a sensitive, rapid means for screening the estrogenic potency of environmentally relevant chemicals and chemical mixtures in vitro.

Induction of hepatic CYP1A in channel catfish increases binding of 2-aminoanthracene to DNA in vitro and in vivo.

Data are presented from in vitro and in vivo studies that indicate cytochrome P4501A (CYP1A) in channel catfish (Ictalurus punctatus) hepatic tissue activates 2-amino-anthracene (AA) to a reactive metabolite that binds to DNA. Channel catfish were injected i.p. with vehicle or 10 mg/kg beta-naphthoflavone (betaNF) on two consecutive days. Two days after the final injection of vehicle or betaNF, vehicle or [3H]AA was injected i.p. at 10 mg/kg, creating four different treatments: vehicle only, betaNF only, [3H]AA only, and betaNF/[3H]AA. Hepatic tissue was examined for CYP1A-associated ethoxyresorufin-O-de-ethylase (EROD) activity, and for DNA adducts at 1, 2, 4 and 7 days following administration of vehicle or [3H]AA. Hepatic EROD activity in betaNF-treated fish was 17-fold higher at day 0 and remained significantly greater than untreated animals for the 7-day experiment. Hepatic DNA adducts, as measured by tritium-associated DNA, ranged from 4.8 to 8.6 pmol/mg DNA in vehicle-pretreated fish injected with [3H]AA, but ranged from 12.6 to 22.7 pmol/mg DNA in betaNF-pretreated fish injected with [3H]AA. Thus, pretreatment with betaNF significantly increased binding of [3H]AA to hepatic DNA in vivo at all four times. Analysis by 32P-post-labeling and thin layer chromatography of hepatic DNA from channel catfish treated with AA revealed two major and several minor spots, which are indicative of DNA adduct formation. Hepatic microsomes from betaNF-pretreated fish were more effective at catalysing the binding of [3H]AA to DNA in vitro than were microsomes from non-treated fish. In addition, binding was decreased by the CYP1A inhibitor 3,3',4,4'-tetrachlorobiphenyl. Collectively, these data demonstrate that CYP1A is involved in the activation of AA in channel catfish.

Comparative in vitro and in vivo benzo[a]pyrene-DNA adduct formation and its relationship to CYP1A activity in two species of ictalurid catfish.

We have measured the formation and persistence of benzo[a]pyrene (BaP)-DNA adducts in the liver of two closely related species of fish, the brown bullhead (Ameriurus nebulosus) and the channel catfish (Ictalurus punctatus) using the 32P-postlabeling method. Liver microsomal ethoxyresorufin-O-deethylase (EROD) activity, arylhydrocarbon hydroxylase (AHH) activity, and in vitro microsome-mediated DNA binding were all significantly higher in the channel catfish. In an in vivo time-course experiment, fish were either induced with beta NF followed by a single BaP i.p. injection (20 mg/kg) or treated with corn oil. BaP-DNA adducts and EROD activity in liver were analyzed 1, 3, 7, 14, and 45 days after the BaP dosage. As in the in vitro experiments, EROD activities in channel catfish were significantly higher at most time points than in bullhead liver (p < 0.05). However, in contrast to the in vitro data, the BaP-DNA adduct profile revealed significantly higher levels of adducts in the bullhead than the channel catfish throughout the time course (p < 0.05). Prior induction with beta NF did not significantly affect the level or type of adduct binding to DNA in either species. Further characterization of the major adduct by HPLC confirmed it to be the anti-BPDE-dGuo adduct. Analysis of tissue distribution of [14C]BaP in the two species suggested similar absorption and initial distribution, but slower elimination from the liver of bullhead than the catfish. The BaP-adduct profiles were consistent with the relative species susceptibility to polycyclic aromatic hydrocarbon-induced liver neoplasia. EROD activities, however, were negatively associated with adduct levels following in vivo exposure.