Biological assessment of bisphenol A degradation in water following direct photolysis and UV advanced oxidation

Endocrine disrupting compounds (EDCs) are exogenous environmental chemicals that can interfere with normal hormone function and present a potential threat to both environmental and human health. The fate, distribution and degradation of EDCs is a subject of considerable investigation. To date, several studies have demonstrated that conventional water treatment processes are ineffective for removal of most EDCs and in some instances produce multiple unknown transformation products. In this study we have investigated the use of direct photolysis with low-pressure (LP) Hg UV lamps and UV+hydrogen peroxide (H(2)O(2)) advanced oxidation process (AOP) for the degradation of a prototypic endocrine disrupter, bisphenol A (BPA), in laboratory water. Removal rates of BPA and formation of degradation products were determined by high performance liquid chromatography (HPLC) analysis. Changes in estrogenic activity were evaluated using both in vitro yeast estrogen screen (YES) and in vivo vitellogenin (VTG) assays with Japanese medaka fish (Oryzias latipes). Our results demonstrate that UV alone did not effectively degrade BPA. However, UV in combination with H(2)O(2) significantly removed BPA parent compound and aqueous estrogenic activity in vitro and in vivo. Removal rates of in vivo estrogenic activity were significantly lower than those observed in vitro, demonstrating differential sensitivities of these bioassays and that certain UV/AOP metabolites may retain estrogenic activity. Furthermore, the UV/H(2)O(2) AOP was effective for reducing larval lethality in treated BPA solutions, suggesting BPA degradation occurred and that the degradation process did not result in the production of acutely toxic intermediates.

Dynamic gene expression changes precede dioxin-induced liver pathogenesis in medaka fish

A major challenge for environmental genomics is linking gene expression to cellular toxicity and morphological alteration. Herein, we address complexities related to hepatic gene expression responses after a single injection of the aryl hydrocarbon receptor (AHR) agonist 2,3,7,8-tetrachlorodibenzo-p-dioxin (dioxin) and illustrate an initial stress response followed by cytologic and adaptive changes in the teleost fish medaka. Using a custom 175-gene array, we find that overall hepatic gene expression and histological changes are strongly dependent on dose and time. The most pronounced dioxin-induced gene expression changes occurred early and preceded morphologic alteration in the liver. Following a systematic search for putative Ah response elements (AHREs) (5'-CACGCA-3') within 2000 bp upstream of the predicted transcriptional start site, the majority (87%) of genes screened in this study did not contain an AHRE, suggesting that gene expression was not solely dependent on AHRE-mediated transcription. Moreover, in the highest dosage, we observed gene expression changes associated with adaptation that persisted for almost two weeks, including induction of a gene putatively identified as ependymin that may function in hepatic injury repair. These data suggest that the cellular response to dioxin involves both AHRE- and non-AHRE-mediated transcription, and that coupling gene expression profiling with analysis of morphologic pathogenesis is essential for establishing temporal relationships between transcriptional changes, toxicity, and adaptation to hepatic injury.

Functional characterization of medaka CYP3A38 and CYP3A40: kinetics and catalysis by expression in a recombinant baculovirus system

Phylogenic analysis of the teleost genomic lineages has demonstrated the precedent for multiple genome duplications. Among many of the genes duplicated, cytochrome P450 genes have undergone independent diversification, which can be traced to a single ancestral gene. In teleosts, cytochrome P450s, from all major families, have been identified. Among these, the CYP3A family has been cloned in several teleost species and demonstrated to contain multiple paralogs differing in gene expression patterns and tissue distribution. Herein we characterized the catalytic and kinetic activities of two medaka CYP3A paralogs (CYP3A38 and CYP3A40) with benzyloxyresorufin (BFC), a fluorescent 3A-selective substrate, and testosterone, a known metabolic substrate for CYP3A enzymes. Recombinant CYP3A was produced using the baculovirus expression vector system in Spodoptera frugiperda (Sf9) and Trichoplusia ni (Tn5) insect cells and accounted for up to 24% of total cellular protein. Following addition of a heme-albumin conjugate to log phase cells, spectral P450 content reached a maximum of 560 and 2350 pmol/mg microsomal protein for CYP3A38 and CYP3A40, respectively. Incubations containing recombinant CYP3A, human NADPH-cytochrome P-450 oxidoreductase reductase, human cytochrome b5, and a NADPH generation system catalyzed the dealkylation of BFC and hydroxylation of testosterone with a high degree of stereoselectivity. However, efficiencies and specificities were significantly different between the two isoforms. Km and Vmax activities based on BFC-catalysis were 0.116 and 0.363 muM, and 7.95 and 7.77 nmol/min/nmol P450 for CYP3A38 and CYP3A40, respectively. CYP3A38 preferentially catalyzed testosterone hydroxylation at the 6beta-, 2beta- and 16beta-positions with minor hydroxylation at other positions within the steroid nucleus. Testosterone catalysis with CYP3A40 was limited predominantly to the 6beta- and 2beta-positions. Putative identification of CYP3A substrate recognition sites (SRS) 1-6 indicates that 12 of the 49 amino acid differences between CYP3A38 and CYP3A40 OFRs occur in SRS regions previously known to be associated with steroid hydroxylation. We suggest that differences in kinetics and catalytic activities are a result of amino acid substitutions in SRS regions 1, 3 and 5 within the CYP3A38 and CYP3A40 protein sequence.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) induces organ- specific differential gene expression in male Japanese medaka (Oryzias latipes)

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a ubiquitous environmental contaminant with well-known adverse effects in fish. In this study, we initially exploited suppression subtractive hybridization (SSH) as a screening tool to assess qualitative gene expression changes in whole brain, liver, and testis of adult male Japanese medaka (Oryzias latipes) exposed for 48 h to a single intraperitoneal-injected dose of TCDD (10 microg TCDD/kg body weight). Across these three organs, SSH identified a total of 335 unique genes. Each set of forward- and reverse-subtracted organ cDNA libraries consisted of a distinct gene list and corresponding distribution of biological processes, suggesting that transcript profiles of these libraries were highly organ-specific. Based on sequence match significance and frequencies within each set of organ libraries, genes hypothesized to be strongly responsive (42 total) within male medaka brain, liver, or testis were semi-quantitatively screened with replicate cDNA nylon membrane arrays. In addition, TCDD-treated male medaka were surveyed for gross histological analysis of brain, liver, and testis. In general, adverse histopathological changes were not observed in the brain, and glycogen depletion was observed only in the liver. However, significant histological changes occurred in the testis, and included disorganization of spermatogenesis at the testis periphery, disruption of the interstitium, Leydig cell swelling, and Sertoli cell vacuolation. Of the 42 genes screened by cDNA array analysis, cytochrome P450 1A (CYP1A) mRNA was the only transcript significantly higher in TCDD-exposed brain, whereas 12 transcripts (including CYP1A) were significantly higher in TCDD-exposed liver, and 34 transcripts were significantly lower in TCDD-exposed testis. Therefore, the degree of TCDD-induced alterations observed in each organ at a gross histological level corresponded well with the number and ontology of gene transcripts affected on the array. Based on real-time reverse transcription polymerase chain reaction (RT-PCR), relative CYP1A (but not AHR1) transcript levels were confirmed to be significantly higher in TCDD-treated brain and liver. However, CYP1A was not significantly induced in TCDD-exposed testis, suggesting that gene expression and histopathological responses observed in the testis at 48 h may be CYP1A-independent. Based on these data, unique liver-specific and testis-specific mRNA-level targets in male medaka were identified as promising biomarkers of acute TCDD-induced toxicity.

Resolving mechanisms of toxicity while pursuing ecotoxicological relevance?

In this age of modern biology, aquatic toxicological research has pursued mechanisms of action of toxicants. This has provided potential tools for ecotoxicologic investigations. However, problems of biocomplexity and issues at higher levels of biological organization remain a challenge. In the 1980s and 1990s and continuing to a lesser extent today, organisms residing in highly contaminated field sites or exposed in the laboratory to calibrated concentrations of individual compounds were carefully analyzed for their responses to priority pollutants. Correlation of biochemical and structural analyses in cultured cells and tissues, as well as the in vivo exposures led to the production and application of biomarkers of exposure and effect and to our awareness of genotoxicity and its chronic manifestations, such as neoplasms, in wild fishes. To gain acceptance of these findings in the greater environmental toxicology community, "validation of the model" versus other, better-established often rodent models, was necessary and became a major focus. Resultant biomarkers were applied to heavily contaminated and reference field sites as part of effects assessment and with investigations following large-scale disasters such as oil spills or industrial accidents. Over the past 15 years, in the laboratory, small aquarium fish models such as medaka (Oryzias latipes), zebrafish (Danio rerio), platyfish (Xiphophorus species), fathead minnow (Pimephales promelas), and sheepshead minnow (Cyprinodon variegatus) were increasingly used establishing mechanisms of toxicants. Today, the same organisms provide reliable information at higher levels of biological organization relevant to ecotoxicology. We review studies resolving mechanisms of toxicity and discuss ways to address biocomplexity, mixtures of contaminants, and the need to relate individual level responses to populations and communities.

Analysis of medaka cytochrome P450 3A homotropic and heterotropic cooperativity

We have previously demonstrated that medaka CYP3A is associated with metabolism of several endobiotics including steroids and bile acids. In this study, we demonstrate that medaka CYP3A catalysis exhibits unusual kinetic behaviors consistent with allosteric interaction which cannot be described by hyperbolic kinetic models. Using 7-benzyloxy-4-(trifluoromethyl)-coumarin (BFC) and nonylphenol as CYP3A substrates, we describe both homotropic and heterotropic cooperative interactions. Given the role of CYP3A in maintaining the homeostatic balance for numerous endobiotics, enzymatic activation/inhibition by endocrine disruptors (EDCs) represents a putative (non-genomic) mechanism for endocrine disruption.

ras oncogene mutations in diethylnitrosamine-induced hepatic tumors in medaka (Oryzias latipes), a teleost fish

Medaka fish are an established non-mammalian research model for the study of liver carcinogenesis and exposure to environmental pollutants. Studies have emphasized the development of hepatic neoplasms in medaka following exposure to model carcinogens. To date however, little information is known regarding the mechanisms underlying initiation of hepatic tumors in this species. The aim of this study was to relate our understanding of diethylnitrosamine (DEN)-induced tumor formation to ras gene activation in hepatic neoplasms of exposed medaka. Initial studies were conducted to identify medaka ras exons 1 and 2 by reverse transcriptase polymerase chain reaction (RT-PCR). Amplification of ras exons 1 and 2 from untreated medaka liver resulted in the identification of three polymorphic ras sequence variants exhibiting a high degree of homology to other teleost and mammalian ras genes. Exposure of medaka to 159 ppm of DEN resulted in a wide range of hepatic neoplasms including: hepatocellular adenomas, hepatocellular carcinomas, cholangiomas, and mixed hepatocholangiocellular carcinomas. Individual liver tumors were examined for oncogenically activating ras mutations by probing genomic DNA with probes specific for activating point mutations or by direct cloning and sequencing of ras transcripts using RT-PCR. Using allele-specific oligonucleotide (ASO) analysis, a single point mutation was detected in codon 12 position two in 8/25 (32%) tumors examined. Mutated ras alleles were additionally detected in 12 of 39 (30%) medaka liver tumors by sequence analysis. Ten of the 12 mutations identified contained a single point mutation at codon 12 resulting in a Gly to Asp amino acid substitution. Two unique mutations were identified at codon 16 resulting in either Lys to Asn or Lys to Thr amino acid substitutions. Our results show that ras mutations are induced by DEN and are present in over 30% of the fish that developed tumors. A ras mutation incidence of 30% is similar to that reported in mammalian species exposed to DEN. While mutations at codon 12 have previously been reported, the present study is the first in vivo report of ras point mutations at codon 16.

Molecular cloning of rainbow trout (Oncorhynchus mykiss) eggshell zona radiata protein complementary DNA: mRNA expression in 17beta-estradiol- and nonylphenol-treated fish

A complementary DNA (cDNA) encoding the eggshell zona radiata protein (RBTZR: AF407574) has been cloned from the liver of estradiol-17beta (E(2))-treated rainbow trout (Oncorhynchus mykiss) by reverse-transcriptase polymerase chain reaction (RT-PCR). A set of degenerate primers homologous to the highly conserved cysteine-rich region of the zona radiata protein gene from salmon, winter flounder, medaka and carp were used for the initial RT-PCR. The resulting PCR product was cloned, sequenced and identified as the Zrp gene fragment based on amino acid sequence similarities. Based on the Zrp sequence from the initial PCR, a pair of gene-sequence primers was designed for 3'- and 5'- random amplification of cDNA ends (RACE). Cloning and sequencing of RACE products showed a 1349-bp Zrp gene encoding a 403-amino acid protein with a theoretical molecular mass of approximately 45 kDa. Alignment of the deduced amino acid sequence reveals that RbtZR is similar to piscine and mammalian zona pellucida proteins. The RbtZR gene, together with the estrogen receptor (ER) and vitellogenin (Vtg) genes, was further characterized and comparatively studied for transcriptional and translational expression in xenoestrogen- (nonylphenol, NP) and E(2)-treated juvenile rainbow trout in a time-course experiment. Northern and slot blot analysis showed that the RbtZR mRNA was expressed, in parallel with the ER and Vtg mRNA, in both NP- and E(2)-treated juvenile rainbow trout. Indirect enzyme-linked immunosorbent assay (ELISA) using monoclonal antibody raised against Atlantic salmon Zrp indicated the translational expression of RbtZR protein in blood plasma samples from NP- and E(2)-treated juvenile trout. The differential time-dependent transcriptional and translational expression and use of Zrp, ER and Vtg as sensitive biomarkers in environmental monitoring of endocrine disrupters in fish is discussed.

Differential biomarker gene and protein expressions in nonylphenol and estradiol-17beta treated juvenile rainbow trout (Oncorhynchus mykiss)

The time- and dose-dependent transcriptional and translational expression of biomarker genes in nonylphenol (NP) and estradiol-17beta (E(2)) treated juvenile rainbow trout is reported. Fish were exposed to NP (1, 5 and 25 mg/kg) and E(2) (5 mg/kg) and killed at 2, 6, 12, 24, 48 and 72 h after exposure. The estrogen receptor (ER), vitellogenin (Vtg) and eggshell zona radiata protein (Zr-protein) gene expressions were analyzed in total liver RNA using Northern and slot hybridization with specific cDNA probes. Plasma Vtg and Zr-protein levels were evaluated using indirect ELISA. While Zr-protein gene showed an induction only at 24 h post-exposure, the plasma protein levels showed a time-dependent increase in the 25-mg NP treated group. Vtg transcripts showed an apparent time-dependent increase without a concomitant increase in protein levels in the 25-mg NP treated fish. Time-dependent increases in Vtg and Zr-protein gene expressions without the corresponding increases in ER gene transcription was observed in E(2)-treated fish at 2, 6 and 12 h post-exposure. Induction of ER gene transcripts was observed from 24 h and did not change significantly at 48 and 72 h. In the E(2)-treated fish, induction of plasma Vtg levels was observed at 48 and 72 h, while plasma Zr-protein was induced at 24, 48 and 72 h, after exposure. We conclude that the E(2)- and NP-induced Vtg and Zr-protein gene expressions at the early time intervals after exposure are not dependent on increase in the transcriptional activity of the ER gene and that Vtg and Zr-protein gene transcriptions require only basal or minimal ER concentration, in addition to other mechanisms.

Identification, characterization, and ontogeny of a second cytochrome P450 3A gene from the fresh water teleost medaka (Oryzias latipes)

Multiple copies of cytochrome P450 gene family 3 have been identified from numerous mammalian species. Often these genes exhibit differential catalytic activities and gene regulation. To date however, little information is available regarding multiple forms of this gene family in teleost fishes. In this study, a second isozyme of cytochrome P450 3A has been cloned from the teleost fish Oryzias latipes and designated CYP3A40. Screening of a cDNA library to medaka liver resulted in the identification of a full length cDNA clone containing a 2316 base pair (bp) insert with an open reading frame encoding a single peptide of 502 amino acids. Comparisons of the deduced amino acid sequence to other known cytochrome P450 sequences indicate that this gene product is most similar to the CYP3A gene family and shares a 90% identity to CYP3A38 previously identified from medaka liver. Consistent with Northern blot and Western blot analysis, Southern blots of medaka genomic DNA demonstrated the presence of two CYP3A genes. Gene expression studies demonstrated that CYP3A38 and CYP3A40 are differentially regulated according to embryonic development. Northern blot analysis, using a probe to a conserved region of both CYP3A genes, demonstrated the presence of a single CYP3A transcript for early and late embryonic stages and two CYP3A transcripts in larvae and adult liver. Similarly, Western blots show a single faint immunoreactive cytochrome P450 3A protein in microsomes from early and late embryos and two abundant protein bands in microsomes from larval and adult liver. To further examine the transcriptional differences in CYP3A expression, RT-PCR analysis was performed on embryonic stages 11-35, 1- and 14-day-old larvae, and adult liver using primer sets specific for CYP3A38 and CYP3A40. These results demonstrate that CYP3A40 is expressed early in embryonic development and continues throughout adult stages. CYP3A38, however, is tightly regulated during embryonic development and is only expressed post-hatch.

Identification and characterization of a cDNA encoding cytochrome P450 3A from the fresh water teleost medaka (Oryzias latipes)

A new member of the CYP3A gene family has been cloned from the teleost fish medaka (Oryzias latipes) by reverse-transcriptase polymerase chain reaction (RT-PCR). Degenerate primers homologous to highly conserved regions of known CYP3A sequences were used for initial RT-PCRs. Individual PCR products were cloned, sequenced, and identified as those belonging to the cytochrome P450 superfamily based on amino acid sequence similarity and the presence of the highly conserved heme-binding region. PCR products were subsequently used as probes to screen a complementary DNA library. A full-length cDNA clone was identified containing a 1758-base-pair (bp) insert with an open reading frame encoding a single peptide of 500 amino acids. Comparisons of the deduced amino acid sequence to other known cytochrome P450 sequences indicate that this gene product is most similar to the CYP3A gene family and has been designated as CYP3A38 by the cytochrome P450 nomenclature committee. Northern blot analysis identified two abundant CYP3A related transcripts in liver of both male and female adults and demonstrated quantitative differences in abundance according to gender. Similarly, Western blot analysis demonstrated the presence of two abundant cytochrome P450 related proteins in liver of both male and female adults. These results suggests that O. latipes contains multiple forms of CYP3A. Heterologous expression of CYP3A38 cDNA in HEK 293 cells produced a single protein that was reactive with anti-scup P450A (CYP3A) polyclonal antibody. Microsomes of HEK 293 cells expressing recombinant CYP3A38 protein actively catalyzed the hydroxylation of testosterone.

Identification of a novel cytochrome P-450 gene from the white rot fungus Phanerochaete chrysosporium

A gene fragment belonging to the cytochrome P-450 superfamily has been cloned and identified from stationary cultures of the filamentous fungus Phanerochaete chrysosporium by reverse transcriptase (RT)-PCR. A set of degenerate primers homologous to highly conserved regions of known cytochrome P-450 sequences were used for initial RT-PCRs. Individual PCR products were cloned, sequenced, and identified as those belonging to the cytochrome P-450 superfamily based on amino acid sequence homologies and the presence of the highly conserved heme binding region. The nucleotide sequence of a single cDNA clone indicated the presence of an open reading frame encoding a partial cytochrome P-450 protein of 208 amino acids. Comparisons of the deduced amino acid sequence of the partial protein to other known cytochrome P-450 sequences indicate that it is the first member of a new family of cytochrome P-450s, designated CYP63-1A. Northern blot analysis suggests that CYP63-1A is expressed under both nitrogen-rich and nitrogen-deficient culture conditions and thus not under the same regulatory constraints as the well-studied lignin and manganese peroxidases. Western blot analyses using antibodies raised to the heme binding region of CYP63-1A indicate that the protein has a molecular mass of approximately 44,000 Da.

Metabolic pathways utilized by Phanerochaete chrysosporium for degradation of the cyclodiene pesticide endosulfan

Recent studies have shown that cultures of white rot fungi not favoring the production of lignin and manganese peroxidases are effective in degrading certain xenobiotics. In this study we have used endosulfan as a model xenobiotic to assess the enzymatic mechanisms of pesticide metabolism under ligninolytic (nutrient-deficient) and nonligninolytic (nutrient-rich) culture conditions. Rapid metabolism of this chlorinated pesticide occurred under each nutrient condition tested. However, the extent of degradation and the nature of the metabolic products differed for nutrient-deficient and nutrient-rich media. The pathways for endosulfan metabolism were characterized by analysis of the fungal metabolites produced. The major endosulfan metabolites were identified by gas chromatography-electron capture detection and gas chromatography-mass spectrometry as endosulfan sulfate, endosulfan diol, endosulfan hydroxyether, and a unknown metabolite tentatively identified as endosulfan dialdehyde. The nature of the metabolites formed indicates that this organism utilizes both oxidative and hydrolytic pathways for metabolism of this pesticide. Piperonyl butoxide, a known cytochrome P-450 inhibitor, significantly inhibited the oxidation of endosulfan to endosulfan sulfate and enhanced hydrolysis of endosulfan to endosulfan diol. We suggest that the metabolism of endosulfan is mediated by two divergent pathways, one hydrolytic and the other oxidative. Judging by the inactivity of extracellular fluid and partially purified lignin peroxidase in metabolizing endosulfan, we conclude that metabolism of this compound does not involve the action of extracellular peroxidases.