Joanna Y. Wilson

Chronic effects of exposure to a pharmaceutical mixture and municipal wastewater in zebrafish.

Pharmaceuticals and personal care products (PPCPs) are discharged in municipal wastewater. Effects in aquatic organisms exposed to individual pharmaceuticals in the laboratory have raised concerns regarding the environmental impacts of PPCPs, yet environmental exposures are always to complex mixtures. In this study, adult zebrafish (Danio rerio) showed significantly decreased embryo production after a 6 week exposure to a pharmaceutical mixture (MIX; 0.5 and 10μgL(-1)) of acetaminophen, carbamazepine, gemfibrozil and venlafaxine and to diluted wastewater effluent (WWE; 5% and 25%). Atretic oocytes and altered ovarian histology were significantly increased in female zebrafish exposed to both concentrations of MIX or WWE, which indicates a direct effect on oocyte development that may account for reduced embryo production. Apoptosis within the thecal and granulosa cell layers was identified in female zebrafish with atresia. Exposures to MIX or WWE at both concentrations severely altered kidney proximal tubule morphology, but no histological impacts on other organs were observed. Exposure of embryos to MIX or WWE at the high concentration significantly increased the incidence of developmental abnormalities. Embryo mortality was elevated with exposure to the high concentration of MIX. These studies indicate that chronic exposure of fish to pharmaceutical mixtures and wastewater impacts reproduction and induces histopathological changes, similar to what we have previously seen with single compound exposures. These data suggest that fish populations exposed to pharmaceuticals discharged in wastewater are at risk of negative impacts to reproductive capacity and health.

Chronic, low concentration exposure to pharmaceuticals impacts multiple organ systems in zebrafish

Pharmaceuticals are found in both receiving and drinking water due to their persistent release in waste-water effluents, raising concerns for environmental and human health. Chronic, aqueous exposure of zebrafish (Danio rerio) to environmentally relevant concentrations of acetaminophen (ACE), venlafaxaine (VEN) (10μgL(-1)), carbamazepine (CBZ) and gemfibrozil (GEM) (0.5 and 10μgL(-1)) decreased reproductive output. Atretic oocytes and altered ovarian histology were seen in female zebrafish exposed to CBZ and GEM, suggesting a direct effect on oocyte development that may account for the reduced fecundity. Apoptosis within the theca and granulosa cells was identified in exposed female zebrafish with atretic oocytes by TUNEL positive staining. The incidence of follicular apoptosis was nearly 2-fold higher in exposed females than the controls. All compounds significantly altered kidney proximal tubule morphology but there was no difference in the incidence of apoptotic cells within the kidney between control and exposed in either males or females. Liver histology was altered by ACE and GEM exposure. Parental exposure to pharmaceuticals did not increase developmental abnormalities, hatching success, or mortality in embryos. Yet, direct exposure of embryos to ACE increased developmental abnormalities and mortality; exposure to 0.5μgL(-1) of all pharmaceuticals increased mortality. CBZ decreased plasma 11-ketotestosterone concentrations in males and females. Overall, these data suggest that low concentration, chronic exposure of fish to pharmaceuticals impacts fish development as well as multiple organ systems in adult fish, leading to effects on reproduction and histology of liver and kidney. These results are significant in understanding the consequences of chronic, low concentration pharmaceutical exposure to fish and suggest that exposed populations are at risk of negative impacts to reproduction and health.

Functional differences in the cytochrome P450 1 family enzymes from Zebrafish (Danio rerio) using heterologously expressed proteins

Mammalian cytochrome P450 1 (CYP1) genes are well characterized, but in other vertebrates only the functions of CYP1A genes have been well studied. We determined the catalytic activity of zebrafish CYP1A, CYP1B1, CYP1C1, CYP1C2, and CYP1D1 proteins using 11 fluorometric substrates and benzo[a]pyrene (BaP). The resorufin-based substrates, 7-ethoxyresorufin, 7-methoxyresorufin, and 7-benzyloxyresorufin, were well metabolized by all CYP1s except CYP1D1. CYP1A metabolized nearly all substrates tested, although rates for non-resorufin substrates were typically lower than resorufin-based substrates. Zebrafish CYP1s did not metabolize 7-benzyloxyquinoline, 3-[2-(N,N-diethyl-N-methylamino)ethyl]-7-methoxy-4-methylcoumarin or 7-methoxy-4-(aminomethyl)-coumarin. CYP1B1 and CYP1C2 had the highest rates of BaP metabolism. 3-Hydroxy-BaP was a prominent metabolite for all but CYP1D1. CYP1A showed broad specificity and had the highest metabolic rates for nearly all substrates. CYP1C1 and CYP1C2 had similar substrate specificity. CYP1D1 had very low activities for all substrates except BaP, and a different regioselectivity for BaP, suggesting that CYP1D1 function may be different from other CYP1s.

Assessment of cytochrome P450 fluorometric substrates with rainbow trout and killifish exposed to dexamethasone, pregnenolone-16α-carbonitrile, rifampicin, and β-naphthoflavone

Cytochrome P450s (CYPs) are important xenobiotic metabolizing proteins. While their functions are well understood in mammals, CYP function in non-mammalian vertebrate systems is much less defined, with function often inferred from mammalian data, assuming similar function across vertebrate species. In this study, we investigate whether in vivo treatment with known mammalian CYP inducers can alter the in vitro catalytic activity of fish microsomes using eleven fluorescent CYP-mediated substrates. We investigate the basal metabolism and induction potential for hepatic CYPs in two fish species, rainbow trout (Oncorhynchus mykiss) and killifish (Fundulus heteroclitus). Species differences were found in the baseline metabolism of these substrates. Killifish have significantly higher metabolic rates for all tested substrates except 7-benzyloxyquinoline and 7-benzyloxy-4-trifluoromethylcoumarin (both mammalian CYP3A substrates); significant differences were also seen between male and female killifish. Treatment with dexamethasone, pregnenolone-16alpha-carbonitrile, and rifampicin did not cause broad, measurable CYP induction in either fish species. In trout, dexamethasone (100 mg kg(-1)) significantly induced 3-cyano-7-ethoxycoumarin metabolism and rifampicin (100 mg kg(-1)) induced the dealkylation of 7-methoxyresorufin, although both were highly variable. Female killifish exposed to pregnenolone-16alpha-carbonitrile (100 mg kg(-1)) showed significantly higher metabolism of 7-pentoxyresorufin. Overall, dexamethasone, pregnenolone-16alpha-carbonitrile and rifampicin did not appear to consistently increase CYP activity in fish. Trout treated with 10 or 50 mg kg(-1) beta-naphthoflavone (BNF), a CYP1A inducer, showed significantly induced activity across almost all substrates tested, exceptions being 7-benzyloxyquinoline, 7-benzyloxy-4-trifluoromethylcoumarin and dibenzylfluorescein. 7-Methoxy-4-(aminomethyl)coumarin, a typical CYP2D substrate in mammals, was not metabolized by untreated fish liver microsomes; however, treatment with BNF significantly induced the metabolism of this substrate in trout. Induced substrate metabolism in BNF-treated microsomes was only correlated across selective substrates, suggesting that BNF induces multiple CYPs in fish liver. These include the known BNF inducible CYP1s plus a number of as yet unidentified fish CYPs. Overall, many of these catalytic assays could be valuable tools for identification of the function of specific CYP subfamilies and individual isoforms in fish.

Assessment of biomarkers for contaminants of emerging concern on aquatic organisms downstream of a municipal wastewater discharge.

Contaminants of emerging concern (CECs), including pharmaceuticals, personal care products and estrogens, are detected in wastewater treatment plant (WWTP) discharges. However, analytical monitoring of wastewater and surface water does not indicate whether CECs are affecting the organisms downstream. In this study, fathead minnows (Pimephales promelas) and freshwater mussels Pyganodon grandis Say, 1829 (synonym: Anodonta grandis Say, 1829) were caged for 4 weeks in the North Saskatchewan River, upstream and downstream of the discharge from the WWTP that serves the Edmonton, AB, Canada. Passive samplers deployed indicated that concentrations of pharmaceuticals, personal care products, an estrogen (estrone) and an androgen (androstenedione) were elevated at sites downstream of the WWTP discharge. Several biomarkers of exposure were significantly altered in the tissues of caged fathead minnows and freshwater mussels relative to the upstream reference sites. Biomarkers altered in fish included induction of CYP3A metabolism, an increase in vitellogenin (Vtg) gene expression in male minnows, elevated ratios of oxidized to total glutathione (i.e. GSSG/TGSH), and an increase in the activity of antioxidant enzymes (i.e. glutathione reductase, glutathione-S-transferase). In mussels, there were no significant changes in biomarkers of oxidative stress and the levels of Vtg-like proteins were reduced, not elevated, indicating a generalized stress response. Immune function was altered in mussels, as indicated by elevated lysosomal activity per hemocyte in P. grandis caged closest to the wastewater discharge. This immune response may be due to exposure to bacterial pathogens in the wastewater. Multivariate analysis indicated a response to the CECs Carbamazepine (CBZ) and Trimethoprim (TPM). Overall, these data indicate that there is a 1 km zone of impact for aquatic organisms downstream of WWTP discharge. However, multiple stressors in municipal wastewater make measurement and interpretation of impact of CECs difficult since water temperature, conductivity and bacteria are also inducing biomarker responses in both fish and mussels.

In vitro inhibition of cytochrome P450-mediated reactions by gemfibrozil, erythromycin, ciprofloxacin and fluoxetine in fish liver microsomes

Inhibition of mammalian cytochrome P450 enzymes (CYPs) is well characterized; major hepatic CYPs can be inhibited by drugs and other environmental contaminants. CYP function and inhibition has not yet been well established in fish yet these studies are important for several reasons. First, such studies will provide functional information for non-mammalian CYPs. Second, specific inhibitors can be used as a diagnostic tool for studying CYP-mediated reactions. Lastly, pharmaceutical mixtures are found in the aquatic environment and adverse effects associated with drug-drug interactions, including CYP inhibition by pharmaceuticals may be of concern. Using liver microsomes from untreated and β-naphthoflavone (BNF)-treated rainbow trout, eight fluorescent CYP-mediated catalytic assays were used to assess in vitro CYP inhibition by four pharmaceuticals: fluoxetine, ciprofloxacin, gemfibrozil and erythromycin. Expressed zebrafish CYP1 proteins (CYP1A, CYP1B1, CYP1C1 and CYP1C2) were assessed for inhibition with selected substrates. All pharmaceuticals decreased the metabolism of a number of substrates. Fluoxetine was the strongest and most broad inhibitor of CYP-mediated reactions in liver microsomes. Zebrafish CYP1s were strongly inhibited by erythromycin and fluoxetine. Although the pharmaceuticals are selective CYP inhibitors in mammals, inhibition across a number of substrates suggests they are broad inhibitors in fish. These data demonstrate that in vitro hepatic CYP inhibition by pharmaceuticals is possible in fish and the patterns seen here are different than what would be expected based on CYP inhibition in mammals.

Cross-species comparison of fluoxetine metabolism with fish liver microsomes

Pharmaceuticals discharged in municipal wastewater are of emerging concern because of their potential for inducing biological effects in aquatic organisms. Selective serotonin reuptake inhibitors (SSRIs), pharmaceuticals prescribed to treat chronic depression, have been detected in receiving and wastewaters. Fluoxetine is a highly prescribed model SSRI used to assess impacts of antidepressants on aquatic organisms. In this study, in vitro hepaticfluoxetine metabolism was determined in several model fish species: rainbow trout, goldfish, zebrafish and killifish. Incubation of fluoxetine with hepatic microsomes from trout pre-treated with carbamazepine showed a time-dependant loss of fluoxetine, concomitant with an increase in norfluoxetine, the major mammalian demethylated metabolite. However, fluoxetine was not well metabolized in reactions with hepatic microsomes from untreated fish. Fluoxetine loss was greater than norfluoxetine production, indicating that norfluoxetine is not the predominant fluoxetine biotransformation product in fish. Furthermore, norfluoxetine was often undetected, possibly indicating that fluoxetine demethylation is a minor metabolic pathway in fish. Inter-species differences in fluoxetine metabolism were not evident because of high intra-species variability, although killifish appeared to have the highest hepatic metabolic capacity for fluoxetine. Fluoxetine metabolism in mammals is catalyzed by cytochrome P450 (CYP) enzymes. Trout were exposed to knownCYP inducers, carbamazepine and 3-methylcholanthrene, to assess potential induction of hepatic fluoxetine metabolism. Microsomes from 3-methylcholanthrene treated fish did not induce detectable changes in fluoxetine concentrations in vitro, indicating that fish CYP1s are not involved in fluoxetine metabolism; the CYPs involved are still unclear. Identification of metabolites other than norfluoxetine warrants further investigation.

Impacts of degraded DNA on restriction enzyme associated DNA sequencing (RADSeq)

Degraded DNA from suboptimal field sampling is common in molecular ecology. However, its impact on techniques that use restriction site associated next‐generation DNA sequencing (RADSeq, GBS) is unknown. We experimentally examined the effects of in situDNA degradation on data generation for a modified double‐digest RADSeq approach (3RAD). We generated libraries using genomic DNA serially extracted from the muscle tissue of 8 individual lake whitefish (Coregonus clupeaformis) following 0‐, 12‐, 48‐ and 96‐h incubation at room temperature posteuthanasia. This treatment of the tissue resulted in input DNA that ranged in quality from nearly intact to highly sheared. All samples were sequenced as a multiplexed pool on an Illumina MiSeq. Libraries created from low to moderately degraded DNA (12–48 h) performed well. In contrast, the number of RADtags per individual, number of variable sites, and percentage of identical RADtags retained were all dramatically reduced when libraries were made using highly degraded DNA (96‐h group). This reduction in performance was largely due to a significant and unexpected loss of raw reads as a result of poor quality scores. Our findings remained consistent after changes in restriction enzymes, modified fold coverage values (2‐ to 16‐fold), and additional read‐length trimming. We conclude that starting DNA quality is an important consideration for RADSeq; however, the approach remains robust until genomic DNA is extensively degraded.

Phylogenetic and Functional Analysis of the Vertebrate Cytochrome P450 2 Family

Cytochrome P450 (CYP) proteins compose a highly diverse superfamily found in all domains of life. These proteins are enzymes involved in metabolism of endogenous and exogenous compounds. In vertebrates, the CYP2 family is one of the largest, most diverse and plays an important role in mammalian drug metabolism. However, there are more than 20 vertebrate CYP2 subfamilies with uncertain evolution and fairly discrete subfamily composition within vertebrate classes, hindering extrapolation of knowledge across subfamilies. To better understand CYP2 diversity, a phylogenetic analysis of 196 CYP2 protein sequences from 16 species was performed using a maximum likelihood approach and Bayesian inference. The analyses included the CYP2 compliment from human, fugu, zebrafish, stickleback, medaka, cow, and dog genomes. Additional sequences were included from rabbit, marsupial, platypus, chicken, frog, and salmonid species. Three CYP2 sequences from the tunicate Ciona intestinalis were utilized as the outgroup. Results indicate a single ancestral vertebrate CYP2 gene and monophyly of all CYP2 subfamilies. Two subfamilies (CYP2R and CYP2U) pre-date vertebrate diversification, allowing direct comparison across vertebrate classes, while all other subfamilies originated during vertebrate diversification, often within specific vertebrate lineages. Analysis of site-specific evolution indicates that some substrate recognition sites (SRS) previously proposed for CYP genes do not have elevated rates of evolution, suggesting that these regions of the protein are not necessarily important in recognition of CYP2 substrates. Type II functional divergence analysis identified multiple residues in the active site of CYP2F, CYP2A, and CYP2B proteins that have undergone radical biochemical changes and may be functionally important.

Signatures of contamination in invasive round gobies (Neogobius melanostomus): A double strike for ecosystem health?

The invasive round goby has a recognised role in transferring contaminants through foodwebs, but little work has been done on contaminant impacts on round gobies themselves. Here we present the first case study of contaminant biomarkers and subpopulation structure variation in round gobies, in relation to habitat contamination, within a Canadian Area of Concern, Hamilton Harbour. Copper and cadmium were elevated in livers of fish from contaminated habitats. Although catch abundances were similar across sites, fish were smaller, a greater proportion of fish were female and more males were in reproductive condition in contaminated sites. Fish from contaminated areas showed more fin loss. Males from contaminated sites showed intersex gonads and genitalia. Ethoxyresorufin-o-deethylase (EROD) activity was higher in fish collected near polycyclic aromatic hydrocarbon (PAH)-rich sediments. The results indicate that contaminants impact the characteristics of round goby populations, which could affect ecosystems beyond toxicant biomagnification. This study also confirms that round gobies can be abundant in polluted habitats, which may draw predators-facilitating mobilisation of contaminants in foodwebs.