A gill filament-based assay for the cytochrome P450 1A (CYP1A)-catalysed activity ethoxyresorufin O-deethylase (EROD) was developed in rainbow trout (Oncorhynchus mykiss) and applied to Atlantic salmon (Salmo salar), Arctic charr (Salvelinus alpinus), Atlantic cod (Gadus morhua), saithe (Pollachius virens), and spotted wolffish (Anarhichas minor). Exposure to waterborne β-naphthoflavone (βNF; 10-6 M) induced branchial EROD activity in all species but the spotted wolffish. In rainbow trout exposed to low concentrations of benzo[a]pyrene (BaP; 10-9 M) and the textile dye indigo (10-8 M) the gills responded more rapidly than the liver to BaP, and indigo induced branchial but not hepatic EROD activity. A CYP1A-dependent BaP adduct formation was shown in gills of fish exposed to waterborne 3H-BaP, i.e. the adduct formation was enhanced by βNF and blocked by ellipticine (CYP1A inhibitor). The predominant location for BaP adducts was the secondary lamellae (most exposed part of the gill filament), whereas the CYP1A enzyme was also present in the primary lamellae of the gill filament. Hence, in addition to the cell-specific expression of CYP1A an important determinant for the localisation of adducts seemed to be the bioavailability of BaP. This idea is supported by the fact that the CYP1A enzyme was induced only in secondary lamellae by BaP (10-7 M) and indigo (10-6 M), whereas it was induced in both primary and secondary lamellae by 3,3´,4,4´,5-pentachlorobiphenyl (10-8 M). Apparently, readily metabolised inducers (BaP and indigo) are biotransformed in the secondary lamellae. My results show that gill filament EROD activity is a sensitive biomarker of exposure to waterborne dioxin-like pollutants, and that the assay has potential for use in monitoring. Furthermore, the results suggest that readily metabolised dioxin-like compounds absorbed via the gills may undergo first-pass metabolism in the gill cells and therefore remain undetected by monitoring of EROD activity in the liver.

Induction of the cytochrome P450(CYP)1A protein and the connected increase in 7-ethoxyresorufin O-deethylase (EROD) activity are common biomarkers in fish. Enhanced activity of this protein signals exposure to Ah-receptor agonists such as chlorinated dioxins, co-planar polychlorinated biphenyls (PCBs) and certain polycyclic aromatic hydrocarbons (PAHs). The EROD biomarker is commonly analyzed in liver microsomes. However, the gill is directly exposed to waterborne pollutants, and in this thesis the gill filament EROD assay was therefore evaluated as a monitoring tool for waterborne CYP1A inducers in fish. Originally developed in rainbow trout (Oncorhynchus mykiss), the assay was here applied in various limnic and marine species. Following exposure to low waterborne concentrations of the readily metabolized CYP1A inducers benzo(a)pyrene (BaP) and indigo, a strong EROD induction was observed in the gill but not in the liver. This likely reflected metabolic clearance of the inducers in gill and other extrahepatic tissues. The high sensitivity of the gill was confirmed in studies of fish caged in waters in urban and rural areas in Sweden where the gill consistently showed a more pronounced EROD induction compared with the liver and the kidney. Fish caged in the reference waters showed surprisingly strong gill EROD induction and CYP1A immunostaining. Consequently, there may be CYP1A inducers present in the aquatic environment that are not yet identified. The assay was further applied in Atlantic cod (Gadus morhua) as a biomarker of exposure to crude oil and produced water (PW) from oil fields in the North Sea. The assay was finally adapted to detect inhibiting compounds, and an imidazole, a triazole and a plant flavonoid turned out to be potent gill EROD inhibitors. The overall conclusion from the studies of this thesis is that the gill filament EROD assay is a practical and sensitive biomarker of exposure to waterborne CYP1A inducers in various fish species. The induction of gill EROD activity in fish also at the reference sites in the field studies calls for further studies on background contamination in Swedish waters.

Pharmaceuticals and personal care products are a growing concern in the aquatic environment. Compounds from the class of non-steroidal anti-inflammatory drugs are commonly detected in surface waters and have the potential to negatively affect aquatic organisms. The purpose of this experiment was to determine the acute and chronic effects of ibuprofen on rainbow trout (Oncorhynchus mykiss). Cyclooxygenase (COX) activity, vitellogenin (VTG) concentration and ethoxyresorufin-O-deethylase (EROD) activity were evaluated following waterborne ibuprofen exposure of trout to 1 and 10 mg/L in the acute exposure and 1, 32 and 1000 μg/L in the chronic exposure, along with an experimental control, E2 control of 1000 μg/L and an E2-ibuprofen mixed treatment. Ibuprofen did not inhibit COX enzyme activity in either gill or kidney tissue. To evaluate the estrogenic effects of ibuprofen, VTG concentrations were measured; by the end of the 56 day chronic exposure VTG concentrations significantly increased in all of the ibuprofen treatments relative to the controls. EROD activity may have been inhibited by ibuprofen but definitive conclusions could not be made. These findings indicate that more research needs to be done studying ibuprofen in aquatic systems. / UOIT

Numerous contaminants are present in mixtures in the aquatic environment. Among these are the azoles, a group of chemicals that includes both pharmaceuticals and pesticides. Azole fungicides are designed to inhibit lanosterol 14-demethylase (cytochrome P450 (CYP) 51), while other azoles are intended to inhibit aromatase (CYP19), i.e. the enzyme catalyzing biosynthesis of estrogens. In fish, a variety of CYP enzymes are involved in biotransformation of waterborne contaminants, and in metabolism of endogenous compounds including steroidal hormones. The induction of CYP1A protein and 7-ethoxyresorufin O-deethylase (EROD) activity are common biomarkers for exposure to aryl hydrocarbon receptor (AhR) agonists in fish. We developed an assay to measure inhibition of CYP1A activity (EROD) in three-spined stickleback and rainbow trout gill tissue ex vivo. Several azole fungicides were found to be potent inhibitors of CYP1A activity. A wastewater effluent containing high concentrations of pharmaceuticals was also shown to inhibit CYP1A activity. Further, several azoles inhibited CYP19 activity in rainbow trout brain microsomes in vitro. Azole mixtures reduced both CYP1A and CYP19 activity monotonically and in an additive way. Given the additive action of the azoles, studies to determine adverse effects of azole mixtures on CYP-regulated physiological functions in fish are needed. Induction of EROD and of gene expression of CYP1 in several organs was observed in an in vivo exposure with the same effluent shown to inhibit EROD. This finding could imply that there was a mixture of AhR agonists and CYP1A inhibitors in the effluent. Finally, wastewater treatment technologies were evaluated using biomarker responses in rainbow trout exposed to effluents of different treatments. The results from chemical analysis together with the biomarker results show that ozone and granulated active carbon treatment removed most pharmaceuticals, as well as AhR agonists and other chemicals present in the regular effluent. This part of the thesis demonstrates that biomarkers in fish such as induction of CYP1 gene expression are applicable to evaluate the efficiency of different treatment technologies for wastewater.

The induction of hepatic cytochrome P4501A1 and its monooxygenase activity 7-ethoxyresorufin O- deethylase, (EROD) in fish by PAHs, PCBs and dioxins has been suggested as an early warning system &ldquo / most sensitive biochemical response&rdquo / for assessing environmental contamination conditions. In this study, the degree of induction of cytochrome P4501A1 protein as determined immunochemically and CYP1A1 associated EROD activity in fish were utilized as biomarkers of exposure to PAHs, PCBs and related organic pollutants along the izmir Bay on the Aegean Sea Coast after the Great Canal Project. Three different fish species were used throughout this study, namely leaping mullet (Liza saliens), annular seabream (Diplodus annularis) and common sole (Solea vulgaris) which were representatives of pelagic, benthopelagic and benthic fish, respectively. Fish were sampled in November 2002 and October 2003 from different sites of the Bay. The mullet caught from Harbor, &Uuml / &ccedil / kuyular port site, and Pasaport region displayed highly elevated EROD activities which were 2258&plusmn / 840 (n=15), 2011&plusmn / 490 (n=4), 1813&plusmn / 287 (n=11) pmole /min/mg protein, respectively and were 104, 80 and 79 fold higher than that of fish obtained from the reference point (25&plusmn / 9 pmole/min/mg protein / n=4). Mullet caught along the pollutant gradient at three other sites (Hekim Island, inciralti, and Zeytinalani) exhibited less but highly significant induced EROD activity. EROD activities of common sole sampled from Fo&ccedil / a open sites (107&plusmn / 20 pmol/min/mg protein, n=5) and site16A (80&plusmn / 12 pmol/min/mg protein, n=9) were found to be very low and the latter was accepted as reference site. The highest EROD activity were seen in fish captured from inciralti which was about 6.3 times higher than those obtained from reference site. Common sole caught from the mouth of Gediz River and Hekim Island exhibited also highly elevated EROD activities. Annular seabream was tested to monitor CYP1A inducing chemicals for the first time in this study. The highest EROD activity (1376&plusmn / 279 pmol/min/mg protein, n=8) were detected in fish samples collected from Harbor region. An inverse relationship was found between distance to the harbor region and EROD activities of annular seabream captured from other sampling sites. In this study for the first time, major cytochrome P450 dependent mixed function oxidase activities such as benzphetamine N- demethylase, ethylmorphine N-demethylase and aniline 4- hydroxylase, were characterized in annular seabream. Changes in the P450 1A1 protein level were determined by immunochemical analysis to monitor the pollutant based induction in all fish species and good correlation was obtained between EROD activity and CYP1A protein content. Fish from polluted sites had both highly induced EROD activity and cytochrome P450 1A content. Chemical analysis of total PAH concentration in sediment and liver tissues of some fish sample were also carried out. Although, izmir Great Canal Project has been active since 2000 to treat and protect the izmir Bay from the contamination of domestic and industrial wastes this study clearly demonstrated that the level of PAH, PCB and dioxin type persistent organic contaminants are still very high especially in the Inner and Middle Bay. This has implications for human fish consumption from contaminated areas, as well as for the health status of aquatic organisms.

The term "biologically active compounds" covers a wide range of substances originating from natural or synthetic origins. These compounds can enter the aquatic environment through wastewater treatment plants, manufactural discharge or they are naturally present in the aquatic plants or microorganisms. Their adverse effects on fish has been widely studied and accepted. This thesis is focussed on the adverse effect of several bioactive compounds (i.e. pharmaceuticals, phytochemicals, or complex mixture of pollutants) on fish using different experimental design as in vitro, in vivo and in situ. In the first part of this thesis, in vitro effects of pharmaceuticals and phytochemicals or their combinations on fish CYP system were investigated. Moreover, effects of standard carrier solvents used in enzyme activity assays were also investigated. An important finding in this study was the lack of effects of either dexamethasone, quercetin, or indole-3-carbinol on EROD activity; however, when these agents were combined, EROD activity was strongly inhibited. This demonstrates that combination of compounds might exert different effects than single compounds, and the effects of mixture compounds cannot be predicted from the effects of individual compounds. In the second part of the thesis, the effects of chronic exposures of rainbow trout to dexamethasone and clotrimazole were investigated. The results regarding dexamethasone showed similarities with in vitro studies, and both in vitro and in vivo exposure of dexamethasone did not alter the CYP enzyme activities. On the other hand, in vivo exposure of clotrimazole yielded conflicting results with findings from the in vitro studies. Clotrimazole induced EROD activity in chronically exposed rainbow trout, and BFCOD activity showed biphasic pattern in which it was inhibited at environmentally relevant concentrations and induced at high concentrations. Thus, the observed effects suggest that clotrimazole could negatively affect fish CYPs at environmentally relevant concentrations. However, in the environment, the effects of clotrimazole and dexamethasone on fish CYPs system might be modified because of unknown compounds in these mixtures. Therefore, further investigations were done to identify the effects of mixture compounds using an in situ model. The last part of the dissertation addresses the effects of cocktail PPCPs on common carp under natural conditions. In situ studies provide valuable information on both hepatic and intestinal CYP activities. Both EROD and BFCOD activities were affected by the PPCPs that are present in the exposed fish. Moreover, changes in intestinal CYP activities suggest that fish can ingest some of these contaminants through their feed. Therefore, the intestines might be responsible for elimination of some of these pollutants and act as the first barrier of pollutant entry in fish. Despite the extensive studies concerning aquatic pollution, further studies are necessary. Development of new pharmaceuticals, their occurrence in the aquatic environment, and their effects on non-target organisms should be continuously monitored.

<p>This thesis reports the results of biomarker measurements in three environmental monitoring projects. In the first project, which was part of the Swedish national environmental monitoring, biomarkers were measured annually in female perch (<i>Perca fluviatilis</i>) in two background areas in the Baltic Sea during 1988–2000, resulting in a unique 13-year series of measurements. The most important results were a strong decreasing temporal trend in the gonadosomatic index (GSI) and a strong increasing temporal trend in the hepatic ethoxyresorufin O-deethylase (EROD) activity in the Baltic Proper. In the second project, biomarkers and concentrations of classic pollutants were measured in female perch in the Stockholm recipient 1999–2001. This was the first time a large city was investigated as a point source of pollution, and the gradient was longer and included more stations than customary. Severe pollution conditions in central Stockholm were indicated by the poor health status of the perch: retarded growth, decreased frequency of sexually mature females, low GSI, disturbed visceral fat metabolism, increased hepatic EROD activity, decreased muscle acetylcholinesterase activity, increased frequency of hepatic DNA adducts, and a high concentration of biliary 1-pyrenol. Muscle ΣDDT and ΣPCB were measured as pollution indicators and were 10–28 respectively 12–35 times higher than the background levels in perch from the Baltic Proper. In the Stockholm archipelago two superimposed gradients were found. Whereas the response of several biomarkers consistently decreased with increasing distance from central Stockholm, the response of others first decreased from Stockholm to the middle archipelago and then increased to the open Baltic Sea. The latter biomarkers included the frequency of sexually mature females, GSI, hepatic EROD activity, and hepatic DNA adducts. In the third project, potential toxicity from munitions on the seafloor, at a dumpsite in the Stockholm archipelago, was analysed by the nanoinjection of sediment extracts into newly fertilised rainbow trout (<i>Oncorhynchus mykiss</i>) eggs, followed by the measurement of biomarkers in the developing larvae. No biological effects of the dumped munitions were found. The same stations in the Stockholm archipelago as in the second project were investigated as a positive control. The results of the three projects agreed well, which demonstrated the continuous pollution of the Baltic Sea and the severe pollution conditions and adverse biological effects in central Stockholm. Further investigations are urgently needed to identify which pollutants or other factors are causing the observed biological effects, both in the background areas in the Baltic Sea and in the Stockholm recipient.</p>

This thesis reports the results of biomarker measurements in three environmental monitoring projects. In the first project, which was part of the Swedish national environmental monitoring, biomarkers were measured annually in female perch (Perca fluviatilis) in two background areas in the Baltic Sea during 1988–2000, resulting in a unique 13-year series of measurements. The most important results were a strong decreasing temporal trend in the gonadosomatic index (GSI) and a strong increasing temporal trend in the hepatic ethoxyresorufin O-deethylase (EROD) activity in the Baltic Proper. In the second project, biomarkers and concentrations of classic pollutants were measured in female perch in the Stockholm recipient 1999–2001. This was the first time a large city was investigated as a point source of pollution, and the gradient was longer and included more stations than customary. Severe pollution conditions in central Stockholm were indicated by the poor health status of the perch: retarded growth, decreased frequency of sexually mature females, low GSI, disturbed visceral fat metabolism, increased hepatic EROD activity, decreased muscle acetylcholinesterase activity, increased frequency of hepatic DNA adducts, and a high concentration of biliary 1-pyrenol. Muscle ΣDDT and ΣPCB were measured as pollution indicators and were 10–28 respectively 12–35 times higher than the background levels in perch from the Baltic Proper. In the Stockholm archipelago two superimposed gradients were found. Whereas the response of several biomarkers consistently decreased with increasing distance from central Stockholm, the response of others first decreased from Stockholm to the middle archipelago and then increased to the open Baltic Sea. The latter biomarkers included the frequency of sexually mature females, GSI, hepatic EROD activity, and hepatic DNA adducts. In the third project, potential toxicity from munitions on the seafloor, at a dumpsite in the Stockholm archipelago, was analysed by the nanoinjection of sediment extracts into newly fertilised rainbow trout (Oncorhynchus mykiss) eggs, followed by the measurement of biomarkers in the developing larvae. No biological effects of the dumped munitions were found. The same stations in the Stockholm archipelago as in the second project were investigated as a positive control. The results of the three projects agreed well, which demonstrated the continuous pollution of the Baltic Sea and the severe pollution conditions and adverse biological effects in central Stockholm. Further investigations are urgently needed to identify which pollutants or other factors are causing the observed biological effects, both in the background areas in the Baltic Sea and in the Stockholm recipient.

Many chemicals present in the aquatic environment can interfere with physiological functions in fish. Exposure to chemicals can be revealed by the use of biomarkers. Induction of 7-ethoxyresorufin O-deethylase (EROD) activity is a commonly used biomarker for exposure to CYP1A inducers such as dioxins and polyaromatic hyrdrocarbons. Vitellogenin is a frequently used biomarker for estrogenic compounds in various fish species whereas a biomarker for androgens, spiggin, is only found in sticklebacks. The main objectives of this thesis were to evaluate gill EROD activity as a biomarker and the three-spined stickleback as a model species in ecotoxicological studies. EROD activities were measured in gill, liver and kidney in rainbow trout (Oncorhynchus mykiss) caged in urban areas in Sweden. EROD induction was most pronounced in the gill. Also in fish caged at reference sites, with an expected low level of known CYP1A inducers, a marked gill EROD induction was found. One suggested inducer in rural waters is humic substances (HS). To evaluate the EROD-inducing capacity of HS, three-spined sticklebacks (Gasterosteus aculeatus) were exposed to HS of natural or synthetic origin. Both kinds of HS caused significant EROD induction. Gill EROD activities were also induced in sticklebacks exposed to ethynylestradiol (EE2) and β-naphthoflavone (βNF), alone and in combinations. Production of vitellogenin was induced in sticklebacks exposed to ≥50 ng EE2/l and a significant decrease in spiggin production was observed in individuals exposed to 170 ng EE2/l. Results from this thesis further strengthen the contention that gill EROD activity is a very sensitive biomarker for CYP1A inducers and that the stickleback is a suitable biomonitoring species, especially for exposure to CYP1A inducers. The finding that not only classical CYP1A inducers but also HS and high EE2 concentrations stimulate gill EROD activity is of significance for the interpretation of biomonitoring data.

L'évaluation de l'impact des polluants dans l'environnement est une des préoccupations majeures qui s'inscrit dans la Directive Européenne Cadre Eau 2000. Les réglementations préconisées ont notamment pour objectif de parvenir au bon état chimique et écologique des masses d'eau. Dans ce contexte, notre étude a consisté à développer une approche multibiomarqueur sur des juvéniles de poisson afin d'évaluer les effets biologiques de la pollution chimique en milieu littoral. Des paramètres moléculaires de détoxification (EROD, GST) et une enzyme antioxydante (CAT) ont été utilisés en tant que "système d'alarme " susceptibles de détecter une perturbation avant l'apparition de signes pathologiques irréversibles. En parallèle, différents biomarqueurs physiologiques (croissance somatique et récente, rapport ARN/ADN, indices morphométrique et lipidique) ont été analysés en considérant que ceux-ci pourraient révéler les dommages induit par les polluants sur l'état de santé des juvéniles. La sensibilité et la pertinence des biomarqueurs moléculaires et physiologiques ont été testés expérimentalement sur des juvéniles : i) de bar exposés à une pollution aigüe de pétrole, ii) de bar et de turbot soumis à des mélanges de contaminants en concentrations environnementales en conditions contrôlée et semi-contrôlée (" caging "). Nos résultats montrent la capacité de l'EROD, et à un degré moindre de la GST, à détecter une exposition courte (2 et 4 jours) des organismes au pétrole et à refléter ses effets délétères sur leur état de santé. Cette relation entre biomarqueurs moléculaires et physiologiques a par contre été plus difficilement établie dans un contexte de pollution multiple. Les indices de croissance et de condition utilisés se sont avérés plus sensibles aux différents niveaux de contamination analysés (métaux et HAPs). Leur utilisation a permis d'évaluer la condition affaiblie des organismes mis en cage en milieu portuaire pendant 38 jours. Cette expérience de " caging " s'est révélée concluante, notamment pour les juvéniles de bar, sur lesquels aucun stress physiologique de la mise en cage n'a été détecté dans la station de référence. Les effets délétères des contaminants chimiques sur l'état de santé des juvéniles de turbot ont également été observés en condition contrôlée après exposition de 21 jours aux mêmes sédiments portuaires et à un sédiment estuarien. En complément de ces expériences, une étude de terrain a été réalisée sur des juvéniles de flet prélevés dans des estuaires le long de la côte française et belge. Une diminution des indices morphométrique et lipidique des juvéniles de flet, issu des trois estuaires anthropisés, a été observée en relation avec des bioconcentrations en métaux plus élevées que l'estuaire de référence. Les résultats issus de ces différentes études montrent la potentialité des indices de croissance et de condition à révéler les effets biologiques des contaminants chimiques sur les juvéniles de poissons marins. Cependant, leur spécificité vis à vis des polluants étant plus faible que les paramètres de détoxification, leur utilisation peut être limitée. Ces travaux montrent ainsi le besoin d'utiliser des biomarqueurs à différents niveaux d'organisation biologique dans les programmes de biosurveillance.