Anguilla anguilla L. liver EROD induction and genotoxic responses after retene exposure

Anguilla anguilla L. (European eel) were exposed for 8, 16, 24, and 72 h to 0 (control), 0.1, 0.3, 0.9, and 2.7 microM retene. A. anguilla L. liver ethoxyresorufin-O-deethylase EROD activity significantly increased during the whole exposure period to all retene concentrations, when compared to their controls. The liver cytochrome P450 content only increased after exposure to high retene concentrations (0.9 and 2.7 microM) from 8 to 24 and 72 h, respectively. Generally, liver DNA integrity decreased with increased retene concentrations. Thus, a low retene concentration (0.1 microM) was only effective at 16 h, 0.3 and 0.9 microM had an early and prolonged effect up to 24h, and 2.7 microM decreased liver DNA integrity during the whole exposure period. However, blood DNA integrity decrease was observed in eels after 24h exposure to 0.1 microM retene, and at 16 h to 0.3 and 0.9 microM retene, despite an early blood DNA integrity decrease at 8 and 16 h exposure to 2.7 microM retene. An early genotoxic response to retene was also observed as erythrocyte nuclear abnormalities plus Notched (ENA+Not) frequency increase at 8, 16, and 24h exposure to 0.1 and 0.3 microM retene as well as at 8, 16, 24, and 72 h to 0.9 microM retene. Though, the highest retene concentration (2.7 microM) only induced ENA+Not and erythrocyte nuclear abnormalities minus Notched (ENA-Not) at 16 h exposure. The eel ENA+Not increase was more sensitive than the ENA-Not increase as a measure of retene genotoxicity. Eel liver alanine amino transferase (ALT) increased activity reveals its enhanced transamination capacity after short-term exposure to retene. The A. anguilla L. ratio between hemoglobin concentration and red blood cells count (Hb/RBC) increased at 8h exposure to 0.1, 0.3, and 0.9 microM retene, suggesting an initial homeostatic process.

Oxidative stress and genotoxic responses to resin acids in Mediterranean mussels

This study represents the first attempt to investigate the genotoxic effects and oxidative stress of resin acids in Mediterranean mussels (Mytilus galloprovincialis Lmk). Mussels were exposed to 2.7 microM abietic acid (AA) and dehydroabietic acid (DHAA) for 6, 12, 18, and 24h. Gill and hepatopancreas conjugation activity, antioxidant defense system, lipid peroxidation (LPO), and DNA damage were determined as reduced glutathione (GSH), glutathione S-transferase (GST) activity, glutathione peroxidase (GPx) activity, catalase (CAT) activity, LPO, and DNA strand breaks. AA caused significant GST inhibition in mussel gills at 12, 18, and 24h. Activity of the antioxidant enzymes, namely, GPx and CAT, was inhibited at 24 and 18 h, respectively, in mussel gills. A significant increase in gill LPO was observed at 24h. The DNA integrity of mussel hepatopancreas significantly decreased after 12 and 24 h exposure to AA. A significant increase in LPO was observed after 6h exposure to DHAA, in either mussel gills or hepatopancreas. DNA integrity was significantly decreased in mussel hepatopancreas after 12 and 24 h exposure to DHAA. AA induced oxidative damage and genotoxicity in mussels, because it promoted increases in LPO in gills and DNA strand breaks in hepatopancreas. DHAA promoted oxidative damage and genotoxicity in mussels, as significant increases were observed in LPO in gills and hepatopancreas and in DNA strand breaks in hepatopancreas.

Physiological and genetic responses of European eel (Anguilla anguilla L.) to short-term chromium or copper exposure-Influence of preexposure to a PAH-like compound

Anguilla anguilla L. (European eel) was exposed for 24 h to chromium (Cr-100 microM and 1 mM) or copper (Cu-1 and 2.5 microM), with or without a 24-h preexposure to beta-naphthoflavone (BNF-2.7 microM), a polycyclic aromatic hydrocarbon (PAH)-like compound, simulating sequential exposure to PAHs and heavy metals. Plasma cortisol, thyroid-stimulating hormone (TSH), free triiodothyronine (T3), and free thyroxine (T4) were determined in order to assess the effects on endocrine function. Plasma glucose and lactate also were measured. The frequency of erythrocytic nuclear abnormalities (ENA) was scored as a genotoxicity indicator. Plasma T4 decreased in eels when exposed to Cr only. The interference of BNF preexposure on Cr effects was observed as a significant plasma glucose increase. Single exposures to Cu elevated plasma cortisol and glucose (2.5 microM), as well as plasma lactate (1 microM), whereas a T4 decrease was found for both concentrations. BNF preexposure prevented plasma cortisol and lactate increases; however, a greater T4 decrease was observed in eels exposed to 2.5 microM Cu. Moreover, this pretreatment was crucial for genotoxicity expression because only BNF+2.5 microM Cu-exposed fish exhibited significant ENA induction. In general, plasma T4 was the most affected hormone, as it responded to all Cr and Cu exposure conditions.

Sparus aurata L. liver EROD and GST activities, plasma cortisol, lactate, glucose and erythrocytic nuclear anomalies following short-term exposure either to 17beta-estradiol (E2) or E2 combined with 4-nonylphenol

Immature Sparus aurata L. (gilthead seabream) were exposed to 17beta-estradiol (E(2)) 4000 ng/l and to the same E(2) concentration mixed with 50,000 ng/l 4-nonylphenol (E(2) + NP) during 4, 8, 12 and 16 h. E(2) availability and E(2) plasma level variations were assessed. Liver biotransformation capacity was measured as ethoxyresorufin-O-deethylase (EROD) and glutathione-S-transferase (GST) activities. Plasma cortisol, lactate and glucose were also determined. Genotoxicity was assessed through erythrocytic nuclear anomalies (ENA) frequency. Liver EROD activity significantly decreased during the whole experiment for both treatments, with the exception of 16 h exposure to E(2). Liver GST activity was significantly increased after 8 and 12 h of exposure either to E(2) or E(2) + NP. An endocrine disruption expressed as plasma cortisol decrease was observed after 16 h exposure under both tested conditions, concomitantly with a plasma lactate increase. No genotoxic responses, measured as ENA frequency, were detected. Analyzing the E(2) water concentration in aquaria without fish it was demonstrated an intense and fast E(2) loss, considerably reducing its availability to fish. In the presence of fish, E(2) water levels were drastically reduced after 4 h exposure, being this reduction more pronounced in E(2) aquarium when compared to E(2) + NP aquarium. In addition, it was demonstrated a rapid E(2) uptake from the water since the highest E(2) plasma concentrations were observed after 4 h exposure, followed by a continuous decrease, which became more pronounced between 8 and 12 h of exposure. Furthermore, during the first 8 h exposure to E(2) and E(2) + NP, seabream plasma E(2) concentrations were higher than the initial water exposure concentration. Comparing the E(2) plasma levels in both seabream-exposed groups, it was clear that its concentration is always higher in E(2) + NP-treated fish. Despite the previous results, no significant differences were found in the measured responses between E(2) and E(2) + NP.

Endocrine and metabolic changes in Anguilla anguilla L. following exposure to beta-naphthoflavone--a microsomal enzyme inducer

Anguilla anguilla L. were exposed during 24 and 48 h to 2.7 muM beta-naphthoflavone (BNF), a known microsomal enzyme inducer. The BNF effects on thyroid-stimulating hormone (TSH), free triiodothyronine (T3), free thyroxine (T4) and cortisol plasma levels were investigated. Alterations on plasma glucose and lactate levels were also measured as an indication of energy-mobilizing hormones alterations. BNF showed to be able to decrease significantly A. anguilla plasma T4 levels, whereas TSH, T3 and cortisol plasma remained constant. However, plasma glucose levels were significantly increased, demonstrating that intermediary metabolism has been affected. These results demonstrate that BNF a PAH-like compound alters the normal functioning of the hypothalamo-pituitary-thyroid (HPT) axis in A. anguilla.

Juvenile sea bass biotransformation, genotoxic and endocrine responses to beta-naphthoflavone, 4-nonylphenol and 17 beta-estradiol individual and combined exposures

Juvenile sea bass, Dicentrarchus labrax L., were exposed during 2, 4, 8, and 24 h to 0.9 microM beta-naphthoflavone (BNF), 131 nM 17 beta-estradiol (E(2)), 4.05 microM 4-nonylphenol (NP), as well as to BNF combined either to E(2) or NP (maintaining the previous concentrations). Liver cytochrome P450 content (P450), ethoxyresorufin-O-deethylase (EROD), and glutathione S-transferase (GST) activities were measured in order to evaluate biotransformation responses. Genotoxicity was assessed as erythrocytic nuclear abnormalities (ENA) frequency. The effects on endocrine function were evaluated as plasma cortisol and glucose. Cortisol was not affected by xeno/estrogens tested, either in single exposure or mixed with BNF. Nevertheless, the intermediary metabolism was affected since glucose concentration increased after 4 h exposure to E(2), and after all BNF+NP exposure lengths. Moreover, a synergism between BNF and NP was thoroughly demonstrated, whereas a sporadic antagonistic interaction was found at 4 h BNF + E(2) exposure. Liver EROD and GST activities were not significantly altered by single E(2) or NP exposure. However, both compounds were able to induce EROD activity in the presence of BNF. NP single exposure was able to significantly increase liver P450 content, while its mixture with BNF displayed an antagonistic interference. Considering the xeno/estrogens single exposures, only NP induced an ENA increase; however, both mixtures (BNF + E(2) and BNF + NP) displayed genotoxic effects. Fish responses to mixtures of xenobiotics are complex and the type of interaction (synergism/potentiation or antagonism) in a particular mixture can vary with the evaluated biological response.

Glutathione protects heavy metal-induced inhibition of hepatic microsomal ethoxyresorufin O-deethylase activity in Dicentrarchus labrax L

The in vitro effects of chromium (Cr(VI)), copper (Cu2+), iron (Fe2+), mercury (Hg2+), and zinc (Zn2+) were assessed on liver microsomal ethoxyresorufin O-deethylase (EROD) activity from a sea bass (Dicentrarchus labrax L.) preexposed under laboratory conditions to 2.7 microM beta-naphthoflavone. The reduced glutathione (GSH) protection potential against heavy metal effects was also studied. The heavy metal concentration ranges used for this study were as follows: 10 pM-5 mM Cr(VI), 10 pM-100 microM Cu2+, 10 pM-1 mM Fe2+, 10 pM-10 microM Hg2+, and 10 pM-100 microM Zn2+. Liver microsomal EROD activity was significantly inhibited after in vitro exposure to Cr(VI) (500 microM), Cu2+ (1 microM), Fe2+ (100 microM), Hg2+ (100 pM), and Zn2+ (10 microM). Heavy metals inhibitory effect on liver EROD activity was ordered as follows: Hg2+ > Cu2+ > Zn2+ > Fe2+ > Cr(VI). Protective effects against Hg2+ (1 and 10 microM), Cu2+ (1, 10, and 100 microM), and Zn2+ (10, 50, and 100 microM) were observed in the presence of 0.5 mM GSH by a decrease in liver microsomal EROD activity inhibition. However, 0.5 mM GSH did not protect liver microsomal EROD activity from Cr(VI), and Fe2+-induced inhibition. The effect of metal mixtures (Cu(2+) + Zn(2+), Zn(2+) + Fe(2+), Zn(2+) + Cr(VI), and Cr(VI) + Fe(2+)) (100 microM) on liver microsomal EROD activity was also assessed, revealing a synergistic interaction.

Anguilla anguilla L. genotoxic and liver biotransformation responses to abietic acid exposure

Adult eels (Anguilla anguilla L.) were exposed for 8, 16, 24, and 72 h to 0, 0.1, 0.3, 0.9, and 2.7 microM abietic acid (AA). Genotoxicity was measured as erythrocytic nuclear abnormalities (ENA), as well as DNA strand breaks in blood and liver. Liver cytochrome P450 (P450) content, liver ethoxyresorufin O-deethylase (EROD), and glutathione S-transferase (GST) activities were determined as biotransformation biomarkers. Liver alanine transaminase (ALT) activity was also measured as an indication of tissue damage. Low AA concentrations, such as 0.1 and 0.3 microM, result in a delayed induction of A. anguilla L. liver EROD activity, whereas the higher AA concentration (2.7 microM AA) also has a delayed effect probably as a consequence of liver tissue high inhibitory concentration. The current eel liver GST activity results demonstrate that only low AA concentrations promote liver increases in GST, whereas high AA concentrations, such as 0.9 and 2.7 microM, do not alter it. The results concerning eel liver ALT activity indicate that significant liver damage is induced by high AA concentrations, such as 2.7 and 0.9 microM. The eel ENA result analysis reveals that AA is a weak ENA inducer in A. anguilla L. Blood DNA integrity results suggest that low AA concentrations promote late decreases in blood DNA integrity; nevertheless, high AA concentrations are early blood genotoxic inducers compared with low AA doses. According to the present research results with respect to eel liver DNA damage, all of the AA exposure concentrations decreased liver DNA integrity.

Anguilla anguilla L. antioxidants responses to in situ bleached kraft pulp mill effluent outlet exposure

This study assesses the antioxidant enzymes activities viz., catalase, glutathione peroxidase, glutathione S-transferase and nonenzymatic antioxidant molecule such as glutathione in Anguilla anguilla L. gill, kidney and liver in response to 8- and 48-h exposure to bleached kraft pulp mill effluent (BKPME). A. anguilla were caged and plunged at three different sites-50 (Site 1), 100 (Site 2) and 2000 m (Site 3) away from the closed BKPME outlet. A significant gill (8 and 48 h) and kidney (48 h) catalase activity decrease was observed at site 2 exposure whereas liver showed a significant increase in catalase activity after 8 and 48 h to site 1 exposure. Glutathione peroxidase (GPX) activity was significantly decreased in gill after 8-h exposure to site 1 and 48-h exposures to sites 1 and 2, respectively. Concerning gill, kidney and liver glutathione S-transferase (GST) activity, a significant gill GST activity decrease after 8 h at site 2 and 48 h at sites 1 and 2 was observed; in kidney, a significant decrease in its activity was observed after 48 h at sites 1 and 2, respectively, whereas in liver, the decrease was significant only at site 2 after 48-h exposure. The in situ BKPME exposure caused a significant total gill and kidney reduced glutathione (GSH) decrease after 8 h at site 2 exposure and after 48 h at site 1 and 2 exposures, respectively. However, a biphasic response was observed in liver, i.e. initial significant increase after 8 h at site 2 followed by a significant decrease after 48 h to the same site exposure. The enzymatic and nonenzymatic antioxidants pattern in gill and kidney, as observed in this study, was different than liver, demonstrating that the liver was more resistant to oxidative damage than gill and kidney. In addition, A. anguilla gill, kidney and liver antioxidants adaptation potentials may serve as a surrogate biomarker to BKPME exposure.

Enzymatic and nonenzymatic antioxidants as an adaptation to phagocyte-induced damage in Anguilla anguilla L. following in situ harbor water exposure

Anguilla anguilla L. were caged for 8 and 48 h in harbor water of Aveiro Lagoon, Portugal. Respiratory burst activity (RBA) of peritoneal, head kidney, and gill phagocytes was measured. Lipid peroxidation (LPO) was estimated in gill, kidney, and liver. Liver ethoxyresorufin-O-deethylase (EROD) activity, cytochrome P450 (Cyt P450) content, and bile metabolites were assayed. Various antioxidant enzymes, viz., glutathione peroxidase, catalase, and glutathione S-transferase and nonenzymatic antioxidant, viz., total reduced glutathione were also studied. Harbor water xenobiotics induced a significant RBA increase in gill after 8 h; whereas in peritoneum and head kidney it increased after 48 h exposure. These responses were adversely associated with tissue-specific peroxidative damage since significant LPO increase was observed in gill (8 and 48 h), kidney (48 h), and liver (48 h). The tissue most affected was gill. Moreover, liver EROD activity, Cyt P450 content and bile metabolites remain unaltered after 8 h; in contrast, 48 h exposure showed significant EROD activity decrease and pyrene-type bile metabolites increase. Decreased EROD activity may be associated with concomitant liver damage, as increased LPO was observed after 48 h. Furthermore, the tissue-specific damage corresponded to the differences in the antioxidant potentials of the tissues, since the initial exposure period caused a significant increase in liver antioxidant activities, whereas gill and kidney showed a significant decrease, demonstrating that liver is highly adaptive to oxidative damage. However, at 48 h exposure gill, kidney, and liver showed a suppressive antioxidant effect, probably due to PAHs, since a significant induction at PAH-type bile metabolites has been seen. Our results demonstrate that phagocyte activation and associated peroxidative damage are concomitantly corroborated with enzymatic and nonenzymatic antioxidant activity differences. In addition, hepatic antioxidant induction after short-term exposure may serve as a potent biomarker for water pollutants in fish.

Anguilla anguilla L. plasma cortisol, lactate and glucose responses to abietic acid, dehydroabietic acid and retene

Anguilla anguilla L. were exposed to 0, 0.1, 0.3, 0.9 and 2.7 microM abietic (AA), dehydroabietic (DHAA) acids and retene (Re) during 8, 16, 24 and 72 h. The eels plasma cortisol, glucose and lactate were measured. A significant decrease in plasma cortisol was observed at 72 h exposure to 0.9 and 2.7 microM Re. DHAA (0.1 microM) significantly decreased plasma cortisol in eels after 8 and 24 h exposure. However, a significant plasma cortisol increase was found after 16 h, 2.7 microM AA exposure and after 24 h exposure to 0.1 microM and 2.7 microM AA. Furthermore, 72 h exposure to 0.9 microM AA also induced a plasma cortisol increase. A general rise in plasma glucose was detected after all exposure periods to Re. The plasma lactate also increased after 72 h exposure to 2.7 microM AA and after 8 h exposure to 0.1 microM DHAA.

Genotoxic and biochemical responses in caged eel (Anguilla anguilla L.) after short-term exposure to harbour waters

European eel (Anguilla anguilla L.) were caged and exposed in situ for 8 and 48 h to the Aveiro offward fishing harbour water (HW) and to clean seawater under laboratory conditions (Control). Eel liver biotransformation (Phase I) was measured as ethoxyresorufin-O-deethylase (EROD) activity, cytochrome P450 (P450) and glutathione S-transferase (GST) activity (Phase II). Genotoxic responses were determined as blood, liver and kidney DNA strand breaks as well as erythrocytic nuclear abnormalities (ENAs). HW failed to significant increase liver EROD, GST activities and ENA frequency. Nevertheless, P450 content was significantly increased after 8 and 48 h exposure. Genotoxicity measured as DNA integrity decrease was found in blood after 8 and 48 h exposure to HW, whereas in liver and kidney, it was observed after 48 h exposure to HW. Blood, kidney and liver genotoxicity may be due to the presence of polycyclic aromatic hydrocarbons (PAHs) which are genotoxic compounds and the main HW organic contaminants.

[Problems in the use of medicines in enterostomized patients]

The practice of intestinal stoma, transitory or permanent, has a series of implications of a physiological, pharmacological, psychological and communitarian character that must be attended to in an integral and individualised way for each patient. Frequently, the ostomised patient is subjected to pharmacological therapy. However, the foreseeable effect of the medicines administered can be affected by factors related to the stoma. Thus, descriptions have been made of extensive resections of ileum that affect the process of the oral absorption of medicines, especially in pharmaceutical forms of enteric covering, delayed release and pills. This would mean access of the unabsorbed portion of the active principle to the collecting device through the faeces and a possible alteration of the duration and intensity of the pharmacological effect. On the other hand, pharmaco surveillance studies have revealed that numerous active principles produce changes in intestinal motility, either on the basis of its fundamental mechanism of action (laxatives, anti-diarrhoea, prokinetics), or as a collateral or secondary effect (antiacids, antidepressants, antihistamines, opioid analgesics). The appearance of constipation and, especially, of diarrhoea can be disturbing and worrying for ostomised patients, and particularly grave in ileostomised patients, due to the dehydration to which it can give rise. Similarly, changes in the colour and odour of faeces, secondary to the administration of medicines (ferrous salts, aluminium hydroxide, bismuth compounds) can needlessly alarm the patients who detect them in the ostomy collecting device (pouch). All these factors can create difficulties for the adhesion of the patient to the proscribed treatment and, as a result, affect its success. However, they can be avoided, corrected or justified with good counselling by the health professionals involved in caring for enterostomized patient.

Genotoxicity biomarkers' association with B(a)P biotransformation in Dicentrarchus labrax L

Dicentrarchus labrax (sea bass) were exposed during 0, 4, 8, 16, 24, 48, and 96 h to 0 and 0.1 microM benzo(a)pyrene (B(a)P), an environmental pollutant, and the following biomarkers were measured: (1) liver cytochrome P450 (P450) content and ethoxyresorufin-O-deethylase (EROD) activity as phase I biotransformation parameters, (2) liver gluthathione-S-transferase (GST) activity as a phase II biotransformation conjugation enzyme, (3) biliary and liver cytosolic B(a)P-type metabolites by fixed wavelength fluorescence detection (FF), and (4) erythrocytic micronuclei (EMN) and erythrocytic nuclear abnormalities (ENA) as genotoxicity biomarkers. Liver EROD activity (4 h), P450 content (24 h), GST activity (4, 8, and 96 h), bile (4-96 h), and liver cytosolic (4-24 h) B(a)P-type metabolites increased significantly in sea bass exposed to B(a)P as well as EMN (8-96 h) and ENA (4-96 h) frequencies. B(a)P genotoxicity is associated with increase in B(a)P-type metabolites in liver cytosol due to an impaired phase II conjugation. This increase seems to be responsible for the decrease in liver EROD and GST activities.

Dicentrarchus labrax biotransformation and genotoxicity responses after exposure to a secondary treated industrial/urban effluent

The present research work was designed to study Dicentrarchus labrax (sea bass) biotransformation and genotoxicity responses to the soluble fraction of a secondary treated industrial/urban effluent (SF-STIUE) discharged through a submarine pipe outlet into the Aveiro coastal area. Sea bass was exposed for 4, 8, 16, 24, 48, and 96 h to 0%, 0.1%, and 1% SF-STIUE and the following biological responses were measured: (1) liver cytochrome P450 (P450) content and ethoxyresorufin-O-deethylase (EROD) activity, as phase I biotransformation parameters; (2) liver gluthathione S-transferase (GST) activity as a phase II conjugation enzyme; (3) biliary and liver cytosol naphthalene (Naph)- and benzo(a)pyrene (B(a)P)-type metabolites, by fixed wavelength fluorescence detection (FF); (4) liver DNA strand breaks, erythrocytic micronuclei (EMN), and erythrocytic nuclear abnormalities (ENA) as genotoxicity parameters. Both SF-STIUE dilutions (0.1% and 1%) failed to significantly increase liver EROD activity, despite a significant increase of liver P450 at 16 and 48 h exposure to 0.1%. Liver GST activity increased significantly at 4h of sea bass exposure to 1% SF-STIUE, being inhibited at 96 h of exposure to this SF-STIUE dilution. Naph- and B(a)P-type metabolite contents were not significantly increased in bile. However, Naph-type metabolite contents increased significantly in liver cytosol at 4h exposure to 1% SF-STIUE, and at 24h exposure to 0.1% and 1% SF-STIUE. Furthermore, B(a)P-type metabolites increased significantly in liver cytosol at 4h exposure to 1% SF-STIUE, and 16 h exposure to 0.1% and 1% SF-STIUE. EMN and ENA frequencies increased significantly at 4, 8, 16, 24, 48, and 96 h exposure to 0.1% and 1% SF-STIUE. Liver DNA integrity decreased significantly at 96 h of sea bass exposure to 1% SF-STIUE. The STIUE discharged into Aveiro coastal area is of great ecotoxicological concern due to its genotoxic potential.

Anguilla anguilla L. liver ethoxyresorufin O-deethylation, glutathione S-transferase, erythrocytic nuclear abnormalities, and endocrine responses to naphthalene and beta-naphthoflavone

The effects of naphthalene (NAP) and beta-naphthoflavone (BNF) on phase I biotransformation and genotoxicity in Anguilla anguilla L. were evaluated. Phase II biotransformation and cortisol levels were also assessed in NAP-treated fish. Two groups of eels were exposed to either a NAP or a BNF concentration range (0.1-2.7 microM) for different exposure periods (2-72 h). An early significant ethoxyresorufin O-deethylation (EROD) activity inhibition was observed, especially for the highest NAP concentrations at 2-6 h exposure and for BNF at 2h exposure. However, a significant EROD activity increase was detected from 16 to 72 h exposure for NAP and from 4 to 72 h exposure for BNF. The cytochrome P450 (P450) content was not dose related. However, with regard to BNF exposure, P450 was the first biomarker to respond. Liver alanine transaminase (ALT) activity was measured as an indicator of hepatic health condition. ALT results demonstrated that the EROD activity decrease, previously described for NAP, was not related to tissue damage. Nevertheless, the highest BNF concentrations were demonstrated to induce liver damage and to impair the EROD activity response. An increased genotoxic response, measured as erythrocytic nuclear abnormalities (ENA), was observed during the first 8h NAP exposure. However, for exposures longer than 8 h, ENA frequency returned to the control levels. This response profile may reflect a considerable DNA repair capacity and/or a metabolic adaptation providing an efficient NAP biotransformation and consequent detoxification. BNF revealed no ENA alterations for all concentrations and exposure lengths. In the NAP experiment a causal relationship between immature erythrocytes (IE) and ENA frequency disappearance was not found. BNF results with regard to IE frequency revealed an ability to alter the balance between erythropoiesis and removal of erythrocytes. Liver glutathione S-transferase activity was significantly induced after 2 and 48 h NAP exposure. A cortisol-impaired response seems to occur from 4 to 24 h NAP exposure, demonstrating an endocrine disruption. However, an adaptation process seems to occur after 48 h, since the plasma cortisol had a tendency to increase. The present findings confirm the usefulness of the adopted biomarkers. The ecological risk associated with aquatic contamination by NAP was also confirmed by the present data.

Genotoxic and hepatic biotransformation responses induced by the overflow of pulp mill and secondary-treated effluents on Anguilla anguilla L

Pulp and paper mill effluent compounds pollute the aquatic environment and are responsible for increased biochemical alterations and genotoxicity in aquatic organisms such as fish. Adult eels (Anguilla anguilla L) were exposed during 8, 16, 24, and 72 h to the following conditions: (1) aerated, filtered, and dechlorinated tap water (C); (2) 2.5% (v/v) sewage water previously treated with activated sludge (T); (3) bleached kraft pulp and paper mill effluent collected at the river Vouga, close to an ancient sewage outlet (Portucel), diluted in tap water [25% (E25) and 50% (E50)]; and (4) bleached kraft pulp and paper mill effluent sediment [water-soluble fraction (S)]. Liver biotransformation induced by the above conditions was measured as ethoxyresorufin-O-deethylase (EROD), cytochrome P450 (P450) (Phase I), and glutathione-S-transferase (GST) (Phase II). Genotoxicity was also determined as blood/liver DNA strand breaks and erythrocytic nuclear abnormalities (ENA) induced on European eel (A. anguilla L). Liver EROD activity was significantly increased in eels at 8 and 16 h exposure to E25, as well as at 16, 24, and 72 h exposure to E50. S exposure induced liver EROD activity only at 24h. A significant decrease in liver P450 was observed at 72 h exposure to T, whereas a significant P450 increase at 16 h was followed by a significant decrease at 24h exposure to E25. Another P450 significant increase was noticed at 72 h exposure to S. Liver GST activity (Phase II) demonstrated a significant increase at 72 h exposure to E50 and to S. A significant decrease in blood DNA integrity was observed at 72 h exposure to T and at 24 and 72 h to S. Blood DNA integrity significantly decreased at 16 and 24 h exposure to E25, as well as at 8, 16, and 24 h exposure to E50. Liver DNA integrity significantly decreased at 72 h exposure to T and at 16 h exposure to S. Moreover, liver DNA integrity was significantly decreased at 24h exposure to E25 and E50, and 72 h to E50. A. anguilla L. increased ENA frequency was detected in T at 16, 24, and 72 h, whereas in E25 and S it was observed at 8, 16, and 24 h. Furthermore, E50 ENA frequency increased at 24 h exposure.

Naphthalene-induced differential tissue damage association with circulating fish phagocyte induction

The effect of naphthalene on phagocytes and associated abnormal cellular activities was studied in Anguilla anguilla L. Fish were exposed to sublethal concentrations (0.1, 0.3, 0.9, 2.7 microM) of naphthalene for 8, 16, 24, 48, and 72 h. Gill, head kidney, and peritoneum phagocyte respiratory burst activity (RBA) was measured by nitroblue tetrazolium reduction assay, whereas lipid peroxidation in fish gill, kidney, and liver was measured by thiobarbituric acid reaction substance. A significant increase (P < 0.05-P < 0.001) in total cell count (TCC) of phagocytes (TCCPH) isolated from gill, head kidney, and peritoneum was observed after 8 h of naphthalene exposure and persisting at 16 h exposure. However, long-term exposures (24, 48, and 72 h) induced a significant (P < 0.05-P < 0.001) decrease in TCC at all the concentration levels. Naphthalene exposure caused a significant (P < 0.05-P < 0.001) RBA induction after 8 and 16 h in gill, head kidney, and peritoneal phagocytes, which consequently resulted in a significant (P < 0.01 and P < 0.001) peroxidative tissue damage increase measured as lipid peroxidation (LPO) in gill, kidney, and liver at the same time intervals. Considering TCCPH, RBA, and LPO, the most affected tissues were gill and kidney after 8 and 16 h exposure to all naphthalene concentrations. RBA was significantly decreased after 24, 48, and 72 h of exposure (P < 0.05-P < 0.001), whereas peroxidative damage increased significantly (P < 0.05-P < 0.001) and persisted in long-term exposures (72 h) at all concentration levels in gill and kidney. Liver short-term exposure (8 and 16 h) to all naphthalene concentrations did not alter LPO activity. Long-term exposures (48 and 72 h) caused a significant (P < 0.01 and P < 0.001) LPO increase, which was more pronounced at 72 h. The results demonstrate that the activation pattern of RBA was corroborated by the extent of phagocyte-induced peroxidative damage in the tissues, as demonstrated by a significant increase of circulating phagocytes. However, the route of exposure and mode of entry of a pollutant may affect the activation pattern of circulating fish phagocytes. It is proposed that measurement of phagocyte-induced reactive oxygen species and their association with peroxidative damage in fish tissues may prove to be useful in biomonitoring fish exposure to aquatic pollutants.

Cortisol, prolactin, growth hormone and neurovegetative responses to emotions elicited during an hypnoidal state

The present study describes the responses of cortisol, prolactin and growth hormone (GH) to emotions elicited during sessions in which an hypnoidal state was induced. The purpose of the study was to provide answers for the following questions: 1) Do sessions with an emotional content have more hormonal surges than baseline, relaxation-only, sessions? 2) Does the induction of a fantasy of pregnancy and nursing elicit a prolactin response? 3) Are there any associations between surges of different hormones? 4) Are hormonal responses related to the intensity, type, or mode of expression of the emotions? For this purpose, thirteen volunteers and twelve patients with minor emotional difficulties were studied during sessions under hypnosis. The period of observation lasted for about three hours. Heart rate (HR), skin conductance (SC) and vagal tone (VT) were monitored. Serum cortisol, prolactin and growth hormone were sampled every 15 minutes. The volunteers had three types of sessions- "blank", consisting of relaxation only (12 sessions), "breast feeding", in which a fantasy of pregnancy and breast feeding was induced (12 sessions) and "free associations" in which the subjects were encouraged to evoke experiences or feelings (17 sessions). The patients had only sessions of free associations (38 sessions). Sessions of free associations had more hormonal surges than "blank" and "breast feeding" sessions. This was true for cortisol (8/17 v.3/24; p < 0.03), prolactin (7/17 v. 3/24; p < 0.05) and GH (9/17 v. 4/24; p < 0.02). During the 55 sessions of free associations (volunteers plus patients) there were 32 surges of cortisol, 18 of prolactin and 28 of GH. Cortisol and prolactin surges were negatively correlated (p < 0.03). GH had no significant association with either cortisol or prolactin. Visible emotions were positively associated with GH surges (p < 0.05). but not with cortisol or prolactin. Cortisol surges were correlated positively with evocations of real events (p < 0.01) and negatively with evocations containing defensive elements (p < 0.01). Cortisol correlated positively with shock and intimidation (p < 0.02) and negatively with rage (p < 0.04). The AUC of the cortisol peaks during shock and intimidation was significantly higher than that of the pool of all other cortisol peaks (12.4 micromol x min x l(-1) v. 7.1 micromol x min x l(-1); p < 0.005). Rage had a marginally significant positive association with prolactin surges (p=0.07). The distribution of GH surges did not show any significant association with types of emotions. The present study provides evidence that cortisol, prolactin and GH respond to psychological stress in humans. However, they are regulated differently from one another. Cortisol and prolactin surges appear to be alternative forms of response to specific emotions. GH surges depend on the intensity of the emotion, probably as a consequence of the associated muscular activity. The current paradigm of stress, implying corticotrophin-releasing hormone (CRH) as the initial step of a cascade of events, is insufficient to account for the diversity of hormonal changes observed in psychological stress in humans.

Nutrient removal from piggery effluent using vertical flow constructed wetlands in southern Brazil

Santa Catarina State, southern Brazil, has the greatest swine breeding activities of Latin America. Generally, the piggery wastewater is treated in pond systems that are able to remove organic material according to local environmental legislation. However, these systems do not remove nitrogen and phosphorus efficiently. This work deals with a post-treatment system, using vertical flow constructed wetlands. The experiment was conducted in a swine production farm which has 45,000 animals. Although the pond system was able to partially remove the content of nutrients, their concentration in the effluent was high for environmental disposal. A four-bed vertical flow constructed wetland pilot plant, using Typha spp., was built. The pilot plant operated for 280 days for beds 2-4 (sand 2). However, the experiments with beds 1-3 (sand 1) were stopped after 111 days of operation, when a reduction in the wastewater drainage was observed. The beds with sand 2 showed a 33% COD removal, and about 49% of nitrification was observed from 111 days until the end of the operation. PO(4)-P removal was 45% with a loading rate of around 1.36 g m(-2) d(-1).

Biotransformation, genotoxic, and histopathological effects of environmental contaminants in European eel (Anguilla anguilla L.)

A prolonged toxicity study was carried out in young European eel (Anguilla anguilla L.) to evaluate the effects of environmental contaminants, namely, two individual standard compounds, benzo[a]pyrene (BaP) and dehydroabietic acid (DHAA), and a complex mixture, bleached kraft pulp mill effluent (BKPME). Fish were exposed to BaP (0.22, 0.45, and 0.9 microM) and BKPME (3.12%, 6.25%, and 12.5% (v/v)) for 3, 7, and 30 days and to DHAA (0.07, 0.15, and 0.30 microM) for 3, 7, 30, 90, and 180 days. The biomarkers include biotransformation and genotoxicity indicators, such as total ethoxyresorufin O-deethylase (EROD) activity and frequency of erythrocytic nuclear abnormalities (ENAs), respectively. Hematological dynamics was assessed as frequency of immature erythrocytes (IEs). Histopathological examinations were carried out for the highest concentrations and for 30 days and longer exposures. Total EROD increases significantly only after 180 days of DHAA exposure. However, significant ENA induction was generally observed during exposure to all contaminants tested. Nevertheless, some of the ENA results suggest an altered genotoxic response, which may arise either from short-term exposures to the highest contaminant levels or long-term exposures to the lowest contaminant levels. IE frequency decreased significantly after 30 days of exposure to 0.45 microM BaP and 180 days of exposure to the entire DHAA concentration range. Increased density of pigmented macrophage aggregates in 30-day BaP- and BKPME-exposed fish as well as in 90- and 180-day DHAA-exposed fish confirmed histopathological liver alterations. Bile accumulation in hepatocytes after BaP treatment, cytoplasmic vacuolization and cell atrophy following DHAA exposure, as well as liver loss of parenchymal cells in BKPME-exposed fish, were also detected. Dispersed necrosis and focal inflammation were observed in the livers of all treated groups. Fish exposed to DHAA and BKPME showed skin and gill disruption as well as kidney Malpighian corpuscle alterations. All 30-day-treated groups revealed intense spleen hemosiderosis, indicating increased erythrophagia. This splenic effect may be strongly correlated with the observed disappearance of ENAs. Neoplastic lesions were not found. A multibiomarker strategy, which includes EROD, ENA, and IE assays as well as histopathological studies, contributed to a better understanding of the global toxic process.

Juvenile sea bass liver biotransformation and erythrocytic genotoxic responses to pulp mill contaminants

This research represents the first study concerning liver phase I biotransformation induction, measured as cytochrome P-450 (P450) and ethoxyresorufin-O-deethylase (EROD), and genotoxic responses, measured as erythrocytic micronuclei (EMN) and nuclear abnormalities (ENA), in Dicentrarchus labrax L. (sea bass) exposed to pulp and paper mill contaminants. Juvenile sea bass were exposed for 6 h to 0 (control) and 0.0125 microM concentrations of the resin acids (RAs) abietic acid (AA) and dehydroabietic acid (DHAA) or 7-isopropyl-1-methylphenanthrene (retene) (Experiment 1). Sea bass were exposed for 6 h to 0 (control), 0.78, 1.56, 3.12, 6.25, and 12.5% bleached kraft pulp mill environmental contaminated water (BKPMECW) collected at the old sewage outlet of a pulp and paper industry (Experiment 2). The time-dependent response was studied in sea bass at 0, 8, 16, 24, 48, and 72 h exposure to 0.78 and 12.5% BKPMECW (Experiment 3). The experimental results demonstrated the presence of genotoxic compounds in BKPMECW. AA, DHAA, and retene may be the constituents responsible for high BKPMECW genotoxicity, since they induced similar sea bass EMN and ENA frequency increases. The BKPMECW, the RAs, and retene failed to significantly increase liver EROD activity and P450 content at 6 h. Furthermore, 3.12% BKPMECW, 0.0125 microM AA, and 0.0125 microM retene significantly decreased liver EROD activity. However, P450 was significantly increased from 8 up to 72 h exposure to BKPMECW. Therefore, the low or inhibited EROD levels could be a consequence of a general membrane disturbance by BKPMECW, RAs, and retene. However, liver ALT results indicate significant liver damage or enzyme inhibition only at 8, 16, 48, and 72 h exposure to BKPMECW.

Naphthalene and beta-naphthoflavone effects on Anguilla anguilla L. hepatic metabolism and erythrocytic nuclear abnormalities

The effects of a polycyclic aromatic hydrocarbon (PAH) such as naphthalene (NAP)--an environmental contaminant--and beta-naphthoflavone (BNF)--a model substance (PAH-like compound)--were investigated in European eel (Anguilla anguilla L.) over 3-, 6-, and 9-day exposure (0.1-2.7 microM). Both xenobiotics revealed to be strong biotransformation (phase I) inducers. After 3-day exposure, liver ethoxyresorufin O-deethylase (EROD) activity was significantly increased by all NAP and BNF tested concentrations. At 6 and 9 days, liver EROD activity was significantly induced mainly by the highest NAP and BNF concentrations. Liver cytochrome P450 content was significantly induced after 3-day exposure to 0.9 and 2.7 microM BNF and 9-day exposure to 0.1, 0.3 and 0.9 microM NAP. Liver alanine transaminase (ALT) activity was measured as an indicator of hepatic health condition, revealing a significant decrease after 6-day exposure to 0.9 microM BNF. Genotoxicity measured as erythrocytic nuclear abnormalities (ENA) was detected in all BNF treated fish on day 6, whereas on day 9, ENA frequencies returned to control levels, significantly decreasing at 0.9 microM BNF exposure. Immature erythrocytes (IE) frequency demonstrated a decreasing tendency along the BNF experiment and concomitantly with the above ENA response. The present experimental results elect EROD activity in A. anguilla as a useful short- to medium-term biomarker of exposure to both PAH and PAH-like compounds. However, some problems can emerge in the presence of high xenobiotic concentrations. Concerning genotoxicity, it is hypothesized that ENA response depends on different factors such as the exhaustion of the detoxification process, the balance erythropoiesis/erythrocytic catabolism and the DNA repairing capacity.

Anguilla anguilla L. biochemical and genotoxic responses to benzo[a]pyrene

Eels (Anguilla anguilla L.) were exposed for 2, 4, 6, 8, 16, 24, 48, 72, 144, and 216 h to 0 (control), 0.3, 0.9, and 2.7 microM benzo[a]pyrene (BaP). The biotransformation induced by BaP was measured as liver ethoxyresorufin O-deethylase (EROD) activity and cytochrome P450 content, and compared with the genotoxic effects, such as erythrocytic nuclear abnormalities (ENA), and blood and liver DNA strand breaks. The liver exhibited a highly significant EROD activity increase from 2 up to 216 h exposure to 0.9 and 2.7 microM BaP, whereas 0.3 microM BaP exposure induced a significant liver EROD increase from 2 up to 144 h. Liver cytochrome P-450 content was significantly increased at 8 h to 2.7 microM BaP exposure. Liver DNA integrity was decreased at 16 h, from 8 up to 144 h and 8 up to 72 h exposure to 0.3, 0.9, and 2.7 microM BaP, respectively. A significant decrease in blood DNA integrity was observed at 48, 72, 144 h, from 8 up to 72, and from 6 up to 72 h exposure to 0.3, 0.9, and 2.7 microM BaP, respectively. The A. anguilla L. genotoxic response to BaP, measured as ENA induction, was significantly increased at 144 h exposure to 0.3 microM BaP. The intermediate BaP concentration tested (0.9 microM) induced a significant three fold ENA increase at 48 and 72 h exposure compared to their controls. The highest BaP concentration (2.7 microM) induced a significant increase in ENA frequency at 72, 144 and 216 h exposure.