Influence of dioxin and metal-contaminated sediment on phase I and II biotransformation enzymes in silver crucian carp

Several biochemical responses were measured in silver crucian carp (Carassius auratus gibelio) after exposure to sediments obtained from contaminated Ya-Er Lake, No, 1 pond, and an unpolluted reference site, Honglian Lake. After 1 week of exposure, a significant induction of the phase I biotransformation enzyme (ethoxylresorufin-o-deethylase, EROD) was found (83-fold of control), whereas the phase II biotransformation enzyme (glutathione S-transferase, GST) exhibited a slight, but significant induction (1,4-fold of control) after 4 weeks of exposure. The level of cellular glutathione in the liver was also slightly elevated after 4 weeks of exposure. The delayed response of GST to the contaminants indicates that the phase I and phase II biotransformation enzymes are regulated differently in fish. The results suggest that EROD is a sensitive bioindicator to assess the toxicity of dioxin-contamined sediment in the laboratory, (C) 1998 Academic Press.

Molecular biomarkers and toxic consequences of impact by organic pollution in aquatic organisms

Organic contaminants are readily bioaccumulated by aquatic organisms. Exposure to and toxic effects of contaminants can be measured in terms of the biochemical responses of the organisms (i.e. molecular biomarkers). The hepatic biotransformation enzyme cytochrome P4501A (CYP1A) in vertebrates is specifically induced by organic contaminants such as aromatic hydrocarbons, PCBs and dioxins, and is involved in chemical carcinogenesis via catalysis of the covalent binding of organic contaminants to DNA (DNA-adducts). Hepatic CYP1A induction has been used extensively and successfully as a biomarker of organic contaminant exposure in fish. Fewer but equally encouraging studies in fish have used hepatic bulky, hydrophobic DNA-adducts as biomarkers of organic contaminant damage. Much less is known of the situation in marine invertebrates, but a CYPlA-like enzyme with limited inducibility and some potential for biomarker application is indicated. Stimulation of reactive oxygen species (ROS) production is another potential mechanism of organic contaminant-mediated DNA and other damage in aquatic organisms. A combination of antioxidant (enzymes, scavengers) and pro-oxidant (oxidised DNA bases, lipid peroxidation) measurements may have potential as a biomarker of organic contaminant exposure (particularly those chemicals which do not induce CYP1A) and/or oxidative stress, but more studies are required. Both CYP1A- and ROS-mediated toxicity are indicated to result in higher order deleterious effects, including cancer and other aspects of animal fitness.

Efeitos genotóxicos e bioquímicos de xenobióticos em animais aquáticos

No presente trabalho, foi estudado um largo espectro de efeitos genotóxicos e bioquímicos na tainha-garrento (Liza aurata). Nos Capítulos II e III são descritos os efeitos de exposição de curta duração ao fenantreno, um hidrocarboneto aromático policíclico (HAP). A exposição de curta duração (16 horas) demonstrou a capacidade deste composto induzir a actividade da enzima de fase I da biotransformação, etoxiresorufina O-desetilase (EROD), provocar decréscimos de integridade no ADN hepático e aumento de anomalias nucleares eritrocíticas (ANE). Em termos de respostas de stresse, os níveis plasmáticos de cortisol e glucose aumentaram face à exposição a este HAP. A exposição ao fenantreno induziu o decréscimo da glutationa peroxidase (GPx) nas guelras, enquanto que no fígado a actividade da GPx aumentou. No rim, a actividade da glutationa S-transferase (GST) foi inibida. Nas guelras, verificou-se um aumento da catalase. O fenantreno demonstrou igualmente a capacidade de induzir um aumento dos níveis de glutationa nas guelras e fígado. Estas respostas demonstraram a sensibilidade de L. aurata, a este HAP, realçando a especificidade das respostas em termos de órgãos. Apesar dos aumentos das defesas antioxidantes, o potencial tóxico deste composto foi demonstrado pelo aumento da peroxidação lipídica nos três órgãos. Nos capítulos seguintes, são descritas as respostas de L. aurata capturada na Ria de Aveiro, em locais com diferentes perfis de contaminação, inicialmente no Outono de 2005 (Capítulos III a IX) e posteriormente analisando respostas sazonais (Capítulos X e XI). A análise de respostas de stresse (cortisol, glucose e lactato) revelou que L. aurata capturada em Vagos (local contaminado por HAPs) apresentava níveis baixos de cortisol, enquanto que no Laranjo (local contaminado por mercúrio) apresentavam elevados níveis de glucose e lactato. Relativamente às hormonas do eixo hipotálamo – hipófise – tiróide (HHT), foram observados elevados níveis plasmáticos da hormona estimuladora da tiróide (TSH) nos organismos capturados no Laranjo, baixos níveis de tiroxina (T4) nos organismos da Barra (local sujeito a tráfego naval) e baixos níveis de triiodotironina (T3) no Rio Novo do Príncipe (próximo de um antigo efluente de pasta de papel), Laranjo e Vagos. A avaliação das defesas antioxidantes, dano oxidativo e genotóxico nas guelras, rim e fígado revelou diferenças significativas nas respostas dos órgãos. L. aurata capturada na Barra apresentou dano oxidativo nas guelras (Capítulo V). No rim foi detectada uma diminuição da integridade do ADN no Rio Novo do Príncipe e Vagos (Capítulo VI), enquanto que no fígado foi observado dano lipídico na Gafanha e Vagos (Capítulo VIII). O dano não esteve sempre associado a um decréscimo das defesas. As análises da água e do sedimento da Ria de Aveiro (Outono de 2005) revelaram elevadas concentrações de metais (Cd, Hg, Cu e Zn),principalmente, no Laranjo e Rio Novo do Príncipe. L. aurata capturada nestes locais apresentou os níveis mais elevados de metalotioninas hepáticas (Capítulo VII) que parecem responsáveis pela inexistência de danos no fígado (Capítulo VIII). O dano oxidativo no ADN, avaliado através da quantificação dos níveis plasmáticos de 8-hidroxi-2-desoxiguanosina (8-OHdG) e o dano clastogénico/aneugénico, avaliado através da quantificação da frequência de ANE, foram estudados, no Outono de 2005, em duas espécies de peixes (L. aurata e Dicentrarchus labrax - robalo) (Capítulo IX). Os resultados revelaram grande sensibilidade de D. labrax em termos de dano oxidativo no ADN na Gafanha, Rio Novo do Príncipe e Vagos, enquanto que L. aurata apresentou dano oxidativo apenas no Laranjo. O aumento da frequência de ANE apenas foi detectado em L. aurata, em Vagos, não se tendo detectado correlação entre estes dois parâmetros. O estudo sazonal (Maio de 2006 a Março de 2007) do dano oxidativo no ADN e frequência de ANE em L. aurata (Capítulo X) demonstrou a variação destes parâmetros com a estação do ano, apesar de não se ter verificado correlação com os parâmetros hidrológicos determinados. No entanto, no local de referência não se verificaram diferenças sazonais, o que sugere que estes biomarcadores reflectem variações de biodisponibilidade de contaminantes. A análise global dos resultados das diferentes estações do ano revelou que L. aurata capturada no Rio Novo do Príncipe e em Vagos apresentou maior susceptibilidade a dano oxidativo no ADN. No entanto, apenas L. aurata capturada em Vagos apresentou frequência de ANE superior à do local de referência. Os dados do estudo sazonal revelaram uma correlação entre dano oxidativo e ANE, sugerindo o stresse oxidativo como um possível mecanismo envolvido na formação de anomalias. A integridade do ADN das guelras, rim, fígado e sangue de L. aurata foi igualmente estudada ao longo de um ano (Capítulo XI), tendo-se verificado uma grande variabilidade ao longo deste período. Não foi demonstrada sensibilidade a um perfil de contaminação específico, tendo-se verificando variabilidade sazonal no local de referência. Globalmente, os resultados demonstraram a importância da utilização de uma bateria de biomarcadores na monitorização ambiental e a especificidade da resposta dos diferentes órgãos de L. aurata.

Biomarcadores genéticos e bioquímicos para avaliar os efeitos do biodiesel, por meio de bioensaios in vivo e in vitro

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Biochemical responses, morphometric changes, genotoxic effects and CYP1A expression in the armored catfish Pterygoplichthys anisitsi after 15 days of exposure to mineral diesel and biodiesel

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Transfer and effects of 1,2,3,5,7-pentachloronaphthalene in an experimental food chain.

Polychlorinated naphthalenes are environmentally relevant compounds that are measured in biota at concentrations in the μg/kg lipid range. Despite their widespread occurrence, literature data on the accumulation and effects of these compounds in aquatic ecosystems are sparsely available. The goal of this study was to gain insights into the biomagnification and effects of 1,2,3,5,7-pentachloronaphthalene (PeCN52) in an experimental food chain consisting of benthic worms and juvenile rainbow trout. Worms were contaminated with PeCN52 by passive dosing from polydimethylsiloxane silicone. The contaminated worms were then used to feed the juvenile rainbow trout at 0.12, 0.25 or 0.50 μg/g fish wet weight/day, and the resulting internal whole-body concentrations of the individual fish were linked to biological responses. A possible involvement of the cellular detoxification system was explored by measuring PeCN52-induced expression of the phase I biotransformation enzyme gene cyp1a1 and the ABC transporter gene abcb1a. At the end of the 28-day study, biomagnification factors were similar for all dietary intake levels with values between 0.5 and 0.7 kg lipid(fish)/kg lipid(worm). The average uptake efficiency of 60% indicated that a high amount of PeCN52 was transferred from the worms to the fish. Internal concentrations of up to 175 mg/kg fish lipid in the highest treatment level did not result in effects on survival, behavior, or growth of the juvenile trout, but were associated with the induction of phase I metabolism which was evident from the significant up-regulation of cyp1a1 expression in the liver. In contrast, no changes were seen in abcb1a transcript levels.

Biotransformation of Substituted Pyridines with Dioxygenase-containing Microorganisms.

A series of 2-, 3- and 4-substituted pyridines was metabolised using the mutant soil bacterium Pseudomonas putida UV4 which contains a toluene dioxygenase (TDO) enzyme. The regioselectivity of the biotransformation in each case was determined by the position of the substituent. 4-Alkylpyridines were hydroxylated exclusively on the ring to give the corresponding 4-substituted 3-hydroxypyridines, while 3-alkylpyridines were hydroxylated stereoselectively on C-1 of the alkyl group with no evidence of ring hydroxylation. 2-Alkylpyridines gave both ring and side-chain hydroxylation products. Choro- and bromo-substituted pyridines, and pyridine itself, while being poor substrates for P. putida UV4, were converted to some extent to the corresponding 3-hydroxypyridines. These unoptimised biotransformations are rare examples of the direct enzyme-catalysed oxidation of pyridine rings and provide a novel synthetic method for the preparation of substituted pyridinols. Evidence for the involvement of the same TDO enzyme in both ring and side-chain hydroxylation pathways was obtained using a recombinant strain of Escherichia coli (pKST11) containing a cloned gene for TDO. The observed stereoselectivity of the side-chain hydroxylation process in P. putida UV4 was complicated by the action of an alcohol dehydrogenase enzyme in the organism which slowly leads to epimerisation of the initial (R)-alcohol bioproducts by dehydrogenation to the corresponding ketones followed by stereoselective reduction to the (S)-alcohols.

Selectivity studies of the benzene cis-dihydrodiol dehydrogenase enzyme from Pseudomonas putida ML2 with Vicinal diol substrates

The enantiopure (1S, 2S)-cis-dihydrodiol metabolites 2B-5B have been obtained in low yield from the corresponding monosubstituted halobenzene substrates 2A-5A, using a wild-type strain of Pseudomonas putida (ML2) containing benzene dioxygenase (BDO). Benzene cis-dihydrodiol dehydrogenase (BCD) from P. putida ML2 and naphthalene cis-dihydrodiol dehydrogenase (NCD) from P. putida 8859 were purified and used in a comparative study of the stereoselective biotransformation of cis-dihydrodiol enantiomers 2B-5B. The BCD and NCD enzymes were found to accept cis-dihydrodiol enantiomers of monosubstituted benzene cis-dihydrodiol substrates 2B-5B of opposite absolute configuration. The acyclic alkene 1,2-diols 10-17 were also found to be acceptable substrates for BCD.

Enzyme-catalysed synthesis and absolute configuration assignments of cis-dihydrodiol metabolites from 1,4-disubstituted benzenes

A series of ten cis-dihydro-diol metabolites has been obtained by bacterial biotransformation of the corresponding 1,4-disubstituted benzene substrates using Pseudomonas putida UV4, a source of toluene dioxygenase (TDO). Their enantiomeric excess (ee) values have been established using chiral stationary phase HPLC and H-1 NMR spectroscopy. Absolute configurations of the majority of cis-dihydrodiols have been established using stereochemical correlation and X-ray crystallography and the remainder have been tentatively assigned using NMR spectroscopic methods but finally confirmed by circular dichroism (CD) spectroscopy. These configurational assignments support and extend the validity of an empirical model, previously used to predict the preferred stereochemistry of TDO-catalysed cis-dihydroxylation of ten 1,4-disubstituted benzene substrates, to more than twenty-five examples.

Contrasting effects of a nonionic surfactant on the biotransformation of polycyclic aromatic hydrocarbons to cis-dihydrodiols by soil bacteria

The biotransformation of the polycyclic aromatic hydrocarbons (PAHs) naphthalene and phenanthrene was investigated by using two dioxygenase-expressing bacteria, Pseudomonas sp. strain 9816/11 and Sphingomonas yanoikuyae B8/36, under conditions which facilitate mass-transfer limited substrate oxidation. Both of these strains are mutants that accumulate cis-dihydrodiol metabolites under the reaction conditions used. The effects of the nonpolar solvent 2,2,4,4,6,8,8-heptamethylnonane (HMN) and the nonionic surfactant Triton X-100 on the rate of accumulation of these metabolites were determined. HMN increased the rate of accumulation of metabolites for both microorganisms, with both substrates. The enhancement effect was most noticeable with phenanthrene, which has a lower aqueous solubility than naphthalene. Triton X-100 increased the rate of oxidation of the PAHs with strain 9816/11 with the effect being most noticeable when phenanthrene was used as a substrate. However, the surfactant inhibited the biotransformation of both naphthalene and phenanthrene with strain B8/36 under the same conditions. The observation that a nonionic surfactant could have such contrasting effects on PAH oxidation by different bacteria, which are known to be important for the degradation of these compounds in the environment, may explain why previous research on the application of the surfactants to PAH bioremediation has yielded inconclusive results. The surfactant inhibited growth of the wild-type strain S. yanoikuyae B1 on aromatic compounds but did not inhibit B8/36 dioxygenase enzyme activity in vitro.

ENANTIOSELECTIVE BACTERIAL BIOTRANSFORMATION ROUTES TO CIS-DIOL METABOLITES OF MONOSUBSTITUTED BENZENES, NAPHTHALENE AND BENZOCYCLOALKENES OF EITHER ABSOLUTE-CONFIGURATION

Enzyme-catalysed kinetic resolution and asymmetric dihydroxylation routes to enantiopure cis-diol metabolites of arenes and benzocycloalkenes of either absolute configuration have been developed using appropriate strains of the bacterium Pseudomonas putida.

Phase I and II biotransformation enzymes and polycyclic aromatic hydrocarbons in the Mediterranean mussel (Mytilus galloprovincialis, Lamarck, 1819) collected in front of an oil refinery

The aim of the present study was to investigate the responses of phase I and II biotransformation enzymes and levels of PAHs in the Mediterranean mussel (Mytilus galloprovincialis, Lamarck, 1819) collected from three sites at different distance from an oil refinery. Phase I enzyme activities as NAD(P)H-cyt c red, NADH ferry red, B(a)PMO and phase II as UDPGT. GST were measured in digestive gland while 16 PAHs (US-EPA) in whole soft tissue. An added value to the data obtained in the present study rely on the RDA analysis which showed close correlations between PAHs levels and phase I enzyme activities in mussels collected in front of the refinery. And again a significant spatial correlation between B(a)P levels and NADPH-cyt c red activities was observed using linear models. No differences among sites for B(a) PMO and phase II GST activities were observed, while the application of UDPGT as biomarkers requires further investigation. (C) 2012 Elsevier Ltd. All rights reserved.

The investigation of the reduction mechanism of the 5a-reductase enzyme of Penicillium decumbens /

The 5a-reductase of Penicillium decumbens ATCC 10436 was used as a model for the mammalian enzyme to investigate the mechanism of reduction of testosterone to 5adihydrotestosterone . The purpose of this study was to search for specific 5a-reductase inhibitors which antagonize prostate cancer . In a whole-cell biotransformation mode, this organism reduced testosterone (1) to 5a-dihydrosteroids (8) and 5aandrostane- 3, 17-dione (9) in yields of 28% and 37% respectively. Control experiments have shown that 5aandrostane- 3, 17-dione (9) can be produced from the corresponding alcohol (8) in a subsequent reaction separate from that catalysed by the 5a-reductase enzyme . Androst-4- ene-3, 17-dione (2) is reduced to give only (9) with a recovery of 80% The stereochemistry of the reduction was determined by 500 MHz ^H NMR analysis of the products resulting from the deuterium labelled substrates. The results were obtained by an analysis of the NOE difference spectra, double-quantum filtered phase sensitive COSY 2-D spectra, and ^^c-Ir 2-D shift correlation spectra of deuterium labelled products. According to the unambiguous assignment of the signals due to H-4a and H-4Ii in 5a-dihydro steroids, the NMR data show clearly that addition of hydrogen to the 4{5)K bond has occurred in a trans manner at positions 413 and 5a. To Study the reduction mechanism of this enzyme, several substrates were prepared as following; 3-methyleneandrost-4-en- 17fi-ol(3), androst-4-en-17i5-ol(5) , androst-4-en-3ii, 17fi-diol (6) and 4, 5ii-epoxyandrostane-3, 17-dione (7) . Results suggest that this enzyme system requires an oxygen atom at the 3-position of the steroid in order to bind the substrate. Furthermore, the mechanism of this 5a-reductase may proceed via direct addition of hydrogen at the 4,5 position without involvement of a carbonyl group as an intermediate.

Investigation of regio- and sterochemistries of microbial biotransformation /

Epoxides can be hydrolyzed by fungi to produce chiral diols. The first part of this thesis presents an investigation of the microbial hydrolysis of aziridines comparable in structure to epoxide biotransformation substrates. Biotransformation of the aziridines 1 -methyl-2-phenyl aziridine, 2- phenylaziridine and N-methyl-7-aza bicyclo[4.1.0] heptane was studied using Beauveria sulfurescens, Aspergillus niger and Diplodia gossypina but no evidence for enzymic hydrolysis was obtained. The hydroxylation reaction performed by the fungus Beauveria sulfurescens ATCC 7159 has been studied for many years and several models describing the hydroxylating pattern exhibited by this fungus have been proposed. The second part of this thesis presents a test of the proposed models. The ability of Beauveria sulfurescens to hydroxylate thirty potential substrates was examined, and the data suggest that none of the earlier proposed models accounts for all of the bioconversion results. A possible explanation is proposed, suggesting that there is more than one enzyme responsible for the hydroxylation reactions performed by Beauveria sulfurescens.