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Although immune endocrine interactions in teleost fish have been shown to involve adrenocorticotropin hormone (ACTH) and cortisol, the involvement of corticotropin-releasing hormone (CRH) has not been demonstrated. The present study investigates whether treatment with bacterial endotoxin (lipopolysaccharide, LPS) modulates brain CRH contents or in vitro CRH release in tilapia (Oreochromis mossambicus). 10 days LPS (Escherichia coli) exposure of juvenile tilapia (4.5 weeks post hatch) via the ambient water increased brain CRH and alpha-MSH content, whereas cortisol contents were not increased. This indicates that the elevation of brain CRH levels were not secondary to activation of HPI-axis. Adult tilapia were treated for 6 days with LPS (intraperitoneally) and were sampled before and after 24 h of confinement. Overall LPS pre-treatment modified the reaction of tilapia to the additional stressor of 24 h confinement, as interactions between LPS treatment and confinement were observed at the level of the hypothalamus (diencephalic CRH content), the pituitary (CRH and alpha-MSH content) and in plasma glucose levels. In vitro, LPS pre-treatment abolished CRH release from telencephalic tissues induced by norepinephrine, one of the CRH secretagogues released during stress in vivo. This effect might be a mechanism of action through which LPS in vivo abolished the up-regulation of telencephalic CRH induced by confinement stress. Our results provide evidence that the role of CRH in immune-endocrine interactions is a phylogenetically old mechanism, and we here demonstrate that LPS molecules are able to locally modulate CRH release in the central nervous system.

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High concentrations (up to 600 pg/ml) of corticotropin-releasing hormone (CRH) were detected in plasma of the teleost fish Oreochromis mossambicus (tilapia) when screening peripheral tissues of tilapia exposed to stress. Notably, the plasma CRH response to stressors in tilapia is much more pronounced than that in higher vertebrates, such as rats. After characterisation by RIA, by spiking plasma with synthetic tilapia CRH and by methanol-acid extraction, it is concluded that the immunoreactive (ir) material in plasma represents tilapia CRH(1-41). Results indicate that a CRH-binding protein is absent in tilapia plasma. Unstressed fish had plasma CRH levels under the limit of detection (<2 pg/ml), but following capture stress plasma CRH levels (170-300 pg/ml) as well as plasma cortisol levels (120 ng/ml) increased rapidly to plateau levels, which were reached after approximately 5 min. Tilapia CRH(1-41) tested at concentrations between 10(-11) and 10(-7) M in vitro did not stimulate the cortisol release from interrenal tissue. Also pretreatment of interrenal tissue with 10(-9) M CRH did not sensitise the cortisol-producing cells to a subsequent ACTH challenge. Forty-eight hours of net confinement or 48 h of cortisol treatment abolished the plasma CRH response and cortisol response to capture stress. The rapidity of the plasma CRH response and its inhibition after 48 h of stress or cortisol treatment point to release by central nervous tissue. Therefore the distribution of glucocorticoid receptors (GRs) in the brain and pituitary of tilapia was investigated. Main GR-ir cell clusters were found in the medial part (Dm) and posterior part of the dorsal telencephalon, in the preoptic region, in the inferior lobe of the hypothalamus and in the cerebellum. We conclude from comparison of CRH brain contents of unstressed and stressed fish that plasma CRH was released by CRH-ir cells located in the lateral part of the ventral telencephalon (Vl), and suggest that the cortisol feedback on CRH release by Vl is mainly exerted via the forebrain Dm region. We propose that CRH is mobilised during stress to fulfil peripheral functions, such as the regulation of circulating leukocytes or of cardiac output, as CRH receptors have been reported in these organs for fish species.

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The quantitative distribution of corticotropin-releasing hormone (CRH) in the brain and pituitary of the fish Oreochromis mossambicus (tilapia) was studied following the validation of a radioimmunoassay. Compared to the pituitary content, the brain contained 20 times more CRH. Eighty percent of the total brain content was located outside the hypothalamus, particularly in the telencephalon. Substantial amounts of CRH were also present in other regions devoid of hypophysiotropic neurons, such as the vagal lobe and optic tectum. Telencephalic and pituitary CRH co-eluted with the tilapia CRH(1-41)standard on reverse phase HPLC. In vitro CRH release by the telencephalon amounted to 5% of its content per hour, whereas release from the pituitary was negligible. We conclude that CRH in the brain of tilapia regulates pituitary and non-pituitary related functions, probably as a neurotransmitter or neuromodulator.

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Various toxicants have previously been held responsible for an impaired capacity of fish from polluted environments to elevate their cortisol levels in response to stress. In the present study we investigated the responses to stress in o'p-DDD [2-(chlorophenyl)-2-(4-chlorphenyl)-1,1-dichloroethane] exposed (given a single, oral dose of 75 mg o'p-DDD/kg fish) and unexposed Arctic charr. After o'p-DDD administration fish were left undisturbed and without being fed for 28 days, when they were subjected to an acute handling stress. At 1, 3, 7 and 23 h following stress, primary (ACTH and cortisol secretion) and secondary (plasma Cl levels and energy mobilisation) components of the stress response were monitored. As the nutritional state of wild fish may influence this potential biomarker response, the fish had been subjected to a restricted feed ration prior to o'p-DDD administration in order to obtain marked within-group variations in condition factor. No effects of o'p-DDD were observed on post-stress hormone secretion (i.e. peak post-stress plasma ACTH and cortisol levels), nor on plasma chloride levels. However, other results obtained provided evidence for a metabolic depression by o'p-DDD, witnessed by consistently lower plasma glucose levels before and after stress in these contaminated fish. This may be related to the finding that during the 30-day period between o'p-DDD administration and stress treatment, toxicant treated fish lost less weight in comparison to their sham-treated counterparts. Nutritional state did not appear to influence the performance of the charr in the present experiment, as correlations between the parameters measured and condition factor or lipid contents on an individual basis in all cases turned out non significant. Overall, the results contrast with those of previous in vivo and in vitro studies on fish, which concluded that comparable headkidney o'p-DDD levels impaired interrenal steroidogenesis. Although we conclude that the effects of o'p-DDD on Arctic charr metabolism were not associated with the stress response, we propose that they may well interfere with the animals' ability to cope with stress in the long term, or may compromise other physiological processes, such as smoltification. Finally, the high level of integration of components involved in the stress response complicates the identification of single stress-sensitive indices as biomarkers applicable in environmental monitoring programmes.

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The effects of increased endogenous cortisol levels were compared with those of sublethal copper exposure in the freshwater common carp, Cyprinus carpio. Fish were exposed to either increased levels of endogenous cortisol (200 ng/ml) or sublethal copper (1.9 microM) alone or were pretreated by elevating plasma cortisol levels prior to copper exposure to assess whether interactions between both treatments occurred. Effects induced by increased cortisol levels included increased Na+/K(+)-adenosine triphosphate (ATPase) activity and increased plasma Na+ and plasma osmolarity, while copper exposure induced anaerobic metabolism, gill damage, decreasing Na+/K(+)-ATPase activity, decreasing plasma ion levels, and blood thickening. Pretreatment of copper-exposed fish with cortisol partially protected these fish by reducing the copper-induced decrease in Na+/K(+)-ATPase activity. Overall, the results obtained in this study argue against a major role for cortisol as an intermediate for the toxic effects of copper.

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Dynamics of adrenocorticotropin (ACTH), alpha melanocyte-stimulating hormone (alpha-MSH), N-acetylated-beta-endorphin (N-ac-beta-END), cortisol, and growth hormone (GH) were investigated in gilthead sea bream (Sparus aurata) stressed by handling plus confinement. As indices of the secondary stress response, plasma levels of glucose, lactate, and plasma ions were monitored. Within 1 h, plasma cortisol and ACTH levels increased above the control values but GH levels decreased. Subsequently, at 24 h cortisol and ACTH levels had declined, but were still higher than in controls, whereas GH levels had recovered after 4 h. Regarding the melanotrope peptides, there were no differences in plasma levels of alpha-MSH and N-ac-beta-END, but pituitary stores of these peptides were severely depleted already after 1 h, as were ACTH stores. Pituitary contents of proopiomelanocortin (POMC)-derived hormones did not show significant differences from 72 h onward. Therefore, the results indicate that both handling and confinement affected the corticotropes of the pars distalis and the melanotropes of the neurointermediate lobe but at different magnitudes. The possible involvement of corticotropin-releasing hormone (CRH) in the regulation of pituitary POMC-producing cell types under these conditions was indicated by the in vitro dose-dependent effect of the peptide on release of ACTH, alpha-MSH, and N-ac-beta-END. The corticocotropes appeared more responsive, and approximately 10-fold more sensitive, to CRH compared with the melanotropes. The ACTH-releasing potency of 1 nM CRH was inhibited 75% following pretreatment of the whole pituitary gland with 400 nM of the CRH antagonist alpha-helical CRH(9-41).

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Plasma levels of cortisol, growth hormone (GH), adrenocorticotropin hormone (ACTH), alpha-melanocyte-stimulating hormone (alpha-MSH), N-acetyl-beta-endorphin, in vitro ACTH-stimulated cortisol secretion, and in vitro corticotropin-releasing hormone (CRH)- and thyrotropin-releasing hormone (TRH)-stimulated ACTH and alpha-MSH secretion were investigated in gilthead sea bream exposed to high stocking density (30 kg m(-3)) for 23 days. Within 3 days after the onset of crowding, plasma levels of cortisol, ACTH, alpha-MSH, and N-acetyl-beta-endorphin were above control values. After 7 days, plasma parameters had returned to control levels, but at 23 days, cortisol, alpha-MSH, and N-acetyl-beta-endorphin levels were again elevated over controls, indicating a long-term activation of the melanotrope cells. In contrast, crowding stress elicited a prolonged reduction in plasma GH levels concomitant with the increased hypothalamus-pituitary-interrenal axis (HPI) activation. Crowding stress enhanced cortisol secretory activity of the unstimulated interrenal cells. However, interrenal tissue from crowded fish in vitro displayed an attenuated response to ACTH stimulation compared with tissue from control fish, indicating a desensitization of these cells to ACTH during crowding. The involvement of pituitary proopiomelanocortin-derived peptides in the HPI axis of sea bream is indicated by the observed modulation of the CRH and TRH responsiveness of the corticotropes and melanotropes in crowded fish. At day 1, when there were crowding-induced plasma increases in ACTH and alpha-MSH, there was an attenuated CRH-stimulated but not TRH-stimulated, ACTH release. However, at that time, CRH- and TRH-induced responses of alpha-MSH secretion, and the unstimulated secretory activity of the MSH cells, were enhanced in crowded sea bream. These data provide evidence for stimulatory roles of multiple hypothalamic (CRH and TRH) and pituitary (ACTH and alpha-MSH) peptides in the activation of the hypothalamus-pituitary-interrenal axis under crowding conditions in sea bream.

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The effect of cortisol on Na(+)/K(+)-ATPase expression in the gill chloride cells of tilapia Oreochromis mossambicus was studied by immunocytochemistry at the light and electron microscope levels. One of three doses of cortisol (low, 125 mg kg(-1 )food; middle, 375 mg kg(-1 )food; high, 750 mg kg(-1) food) was administered via the food (at a ration of 1.5 % of body mass) and the fish were sampled after 5 days. Plasma osmolality and Na(+) levels were elevated in the middle- and high-dose groups, and plasma cortisol levels in the high-dose groups. Hematocrit values were not affected by the treatments. Opercular membrane chloride cell density increased by 94 % and 286 % in the middle- and high-dose fish, respectively, whereas the gill chloride cell frequency increased by up to 28 % maximally in the high-dose fish. Lamellar gill chloride cells were absent in the control and low-dose groups, but were observed in the middle- and high-dose groups. Cortisol increased the volume of the tubular membrane system in mature gill chloride cells. Quantification of immunogold-labelled Na(+)/K(+)-ATPase antigen (a 104 kDa protein species, as demonstrated by western blot) revealed that the high dose of cortisol increases the Na(+)/K(+)-ATPase density in the tubular system of chloride cells. This is the first direct evidence that cortisol not only increases chloride cell numbers but also Na(+)/K(+)-ATPase density in these cells.

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Arctic charr were allowed to interact in groups of three for 5 days. Skin darkness was quantified by measuring the mean brightness of individual fish before and after social interaction. Brain levels of monoamines and monoamine metabolites and plasma concentrations of cortisol, adrenocorticotropic hormone (ACTH), N-acetyl-(beta)-endorphin and alpha-melanocyte-stimulating hormone (alpha-MSH) were analysed. The results show that social subordination resulted in a significant skin darkening. Furthermore, plasma concentrations of alpha-MSH, ACTH and cortisol were elevated in subordinates, and these fish also displayed elevated levels of 5-hydroxyindoleacetic acid (5-HIAA) in the telencephalon. The ratio of [5-HIAA] to serotonin [5-HT] was increased in several brain areas. In addition, the ratio of 3-methoxy-4-hydroxyphenylglycol (MHPG) to norepinephrine (NE) concentrations was significantly increased in the optic tectum of subordinate fish. Skin darkness following social interaction showed a significant positive correlation with plasma levels of alpha-MSH. Plasma levels of ACTH and alpha-MSH were both positively correlated with that of cortisol. Brain [5-HIAA]/[5-HT] ratios were positively correlated with circulating plasma levels of ACTH, and a similar positive correlation was seen between [MHPG]/[NE] ratios in the optic tectum and plasma levels of ACTH, alpha-MSH and N-acetyl-beta-endorphin. In contrast, hypothalamic [MHPG]/[NE] ratios displayed a negative correlation with plasma alpha-MSH concentrations. The present study demonstrates that social stress induces skin darkening in Arctic charr and that this effect could be mediated by a stress-induced increase in the levels of alpha-MSH in the circulation. Furthermore, the results suggest that 5-HT and NE in the central nervous system could be factors regulating the pituitary release of ACTH and alpha-MSH.

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Although hypothalamic corticotropin-releasing hormone (CRH) is involved in the stress response in all vertebrate groups, only a limited number of studies on this neuroendocrine peptide deals with non-mammalian neuroendocrine systems. We determined the cDNA sequence of the CRH precursor of the teleost Oreochromis mossambicus (tilapia) and studied the biological potency of the CRH peptide in a homologous teleost bioassay. Polymerase chain reaction (PCR) with degenerate and specific primers yielded fragments of tilapia CRH cDNA. Full-length CRH cDNA (988 nucleotides) was obtained by screening a tilapia hypothalamus cDNA library with the tilapia CRH PCR products. The precursor sequence (167 amino acids) contains a signal peptide, the CRH peptide and a motif conserved among all vertebrate CRH precursors. Tilapia CRH (41 aa) displays between 63% and 80% amino acid sequence identity to CRH from other vertebrates, whereas the degree of identity to members of the urotensin I/urocortin lineage is considerably lower. In a phylogenetic tree, based on alignment of all full CRH peptide precursors presently known, the three teleost CRH precursors (tilapia; sockeye salmon, Oncorhynchus nerka; white sucker, Catostomus commersoni) form a monophyletic group distinct from amphibian and mammalian precursors. Despite the differences between the primary structures of tilapia and rat CRH, maximally effective concentrations of tilapia and rat CRH were equally potent in stimulating adrenocorticotropic hormone (ACTH) and alpha-MSH release by tilapia pituitaries in vitro. The tilapia and salmon CRH sequences show that more variation exists between orthologous vertebrate CRH structures, and teleost CRHs in particular than previously recognized. Whether the structural differences reflect different mechanisms of action of this peptide in the stress response remains to be investigated.

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The responses of rainbow trout and brown trout to the same stressor were compared by measuring primary and secondary stress responses during and after a 5.5-h net confinement. Basal levels of adrenocorticotropic hormone (ACTH), alpha-melanocyte-stimulating hormone (alpha-MSH), and glucose were higher in brown trout than in rainbow trout. While confinement induced transient increases in plasma ACTH and cortisol levels in both species, the magnitude of these responses, but not the time course, was greater in brown trout. Brown trout, but not rainbow trout, showed a reduction in plasma alpha-MSH levels after 5.5 h confinement before returning to control values, and the glucose levels in the brown trout were elevated throughout the confinement and recovery periods. Confinement also resulted in increased hematocrit values and reduced plasma sodium and chloride levels in both species. Rainbow trout appeared to recover faster from the confinement, as glucose and hematocrit values in the brown trout remained elevated and ionoregulatory disturbances persisted even after 46 h. During recovery effects on the immune system were more pronounced in brown trout than in rainbow trout. Circulating white blood cell numbers were reduced in both species following 23 h recovery, but remained low in the brown trout. Elevated alternative complement activity and oxygen radical production were found after 23 h recovery, and reduced lysozyme activity was found after 46 h, in brown trout only. Results indicate that differences in the stress response of these closely related species, as illustrated by the intensity of the cortisol response, originate at the level of the pituitary and are also manifested through secondary stress responses.

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Whole-body levels of ACTH, alpha-MSH and cortisol in eggs and larvae of the common carp (Cyprinus carpio) were determined periodically up until 168 h after fertilisation. ACTH, alpha-MSH and cortisol immunoreactivity was detected in unfertilised eggs, and endogenous production of ACTH and alpha-MSH was observed 24 h after fertilisation and that of cortisol 36 h after fertilisation. ACTH immunoreactivity reached peak levels before hatching (56-72 h after fertilisation) and remained relatively stable thereafter, while alpha-MSH immunoreactivity started to increase after hatching. At 36 h after fertilisation, whole-body cortisol levels increased rapidly reaching peak levels at the end of hatching (72 h after fertilisation), remaining stable until the end of the experiment. From 50 h after fertilisation onwards, embryos and larvae increased their whole-body cortisol levels when subjected to handling (mechanical pressure during egg stage or netting during the larval stage). It is concluded that the pituitary-interrenal axis in carp is fully functional at the time of hatching. No indications of a stress non-responsive period after hatching were observed. To characterise ACTH and alpha-MSH immunoreactivities in carp larvae, whole-body homogenates were analysed by HPLC, with pituitary homogenates of adult carp serving as a reference. ACTH and alpha-MSH immunoreactivity in carp larvae homogenates consisted of three and two products respectively. HPLC of adult carp pituitaries revealed the presence of two ACTH immunoreactive products, which may represent a phosphorylated and a non-phosphorylated ACTH variant, while the three alpha-MSH peaks most likely represent des-acetylated, mono-acetylated and di-acetylated alpha-MSH, the latter being the predominant form. In carp larvae, however, one of the ACTH immunoreactive products co-eluted with the non-phosphorylated ACTH, while the two alpha-MSH products identified co-eluted with des-acetylated and mono-acetylated alpha-MSH, indicating that POMC processing at this stage of development is different from prohormone processing in adult fish.

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Activation of the hypothalamus-pituitary-interrenal (HPI) axis is characteristic of stress responses, which may result from a variety of environmental challenges. To investigate whether the stress response, and in particular the HPI axis, in tilapia (Oreochromis mossambicus) is compromised by short-term exposure to PCB 126, fish of both sexes were fed diets containing PCB 126 (50 microg/kg fish . day) for 5 days. In the first approach, which was performed twice, fish were acutely stressed for periods varying between 1 and 30 min at the end of the exposure period; in the second approach fish were sampled at the end of the exposure period either at rest or after 2 h of stress (confinement). After 5 days, the body weights in all experiments were significantly lower in PCB-fed fish than in control fish. There were no changes in basal plasma glucose levels, plasma ion concentrations, or branchial, renal, and intestinal Na,K-ATPase activity following PCB exposure. In the first experimental approach, in which fish experienced acute sampling stress, plasma cortisol levels reached lower levels in PCB-fed fish than in controls. This suggests an impaired ability to acutely activate interrenal steroidogenesis in PCB-treated tilapia. Adrenocorticotropic hormone (ACTH)- and cAMP-stimulated in vitro cortisol release from superfused head kidneys was lower in tissues from tilapia exposed to PCB 126 than in tissues from control animals. This effect persisted after 24 h in vitro, which, together with the high PCB 126 concentrations measured in the head kidneys of PCB-fed fish, may indicate direct toxic effects on the interrenal cells. The second experimental approach demonstrated that basal plasma cortisol and ACTH levels were not influenced by PCB treatment, but that the basal ACTH content of the rostral pars distalis (RPD) of the pituitary gland of PCB-fed fish was lower than that of control fish. After 2 h confinement, plasma cortisol levels and ACTH content of the RPD rose to similar values in both groups, whereas plasma ACTH levels were higher in confined PCB-fed fish than in confined controls. PCB-fed fish showed a lower hyperglycemic response to confinement than control fish. Confinement resulted in similarly elevated renal and intestinal Na,K-ATPase activities in both PCB-fed and control fish; branchial enzyme activities were not affected. Since PCB did not affect Na,K-ATPase activities and plasma ion concentrations, it is concluded that the effects of PCB 126 on the HPI axis in tilapia are not secondary to ionoregulatory dysfunction.

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Estradiol-17 beta (E), 11-ketotestosterone (KT), and testosterone (T) were administered to immature rainbow and brown trout by implantation of steroid-containing cocoa butter pellets. This procedure elevated the levels of these hormones in the blood of the treated fish and had significant effects on plasma ACTH and cortisol levels in both unstressed and stressed rainbow trout and in stressed brown trout. E treatment significantly elevated resting levels of ACTH and cortisol and KT significantly suppressed resting ACTH levels in rainbow trout, although no effect of KT was noted on baseline cortisol levels. One hour of confinement stress increased ACTH levels in rainbow trout, but less so in T- and KT-implanted fish than in sham-implanted fish. A similar pattern was observed in stress-induced plasma cortisol levels where T and KT treatment of rainbow trout resulted in a more than 50% attenuation of plasma cortisol levels while E implantation significantly increased stress-induced plasma cortisol levels. In brown trout subjected to confinement stress for 96 hr, within 1 hr of the onset of confinement the stress-induced increase in plasma ACTH and plasma cortisol was significantly lower in T- and KT-implanted fish than in sham-implanted controls. However, these differences were not sustained at subsequent sample points during the 96-hr period of continuous confinement. Nonetheless, overall mean ACTH levels for the entire confinement period were significantly enhanced in E-implanted brown trout and significantly reduced in KT-implanted fish. Overall mean cortisol levels were significantly lower in T- and KT-implanted fish. The enhancement of stress responsiveness observed in E-treated immature fish was not observed during confinement stress in untreated mature female trout, with naturally high plasma E levels. However, untreated mature male trout displayed a significantly reduced cortisol response to confinement. It is suggested that gonadal steroids are involved in the regulation of both baseline and stress-induced activity of the pituitary-interrenal axis in salmonid fish.

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In higher vertebrates, two opposite behavioral coping strategies can be distinguished that are associated by a typical neuroendocrine pattern. Little is known about the individual variation in the stress response in lower vertebrates such as teleosts. In the present study, rainbow trout were fitted with an indwelling aortic catheter for repeated blood sampling and exposed to severe hypoxia and subsequent recovery and their behavior was characterized semiquantitatively during hypoxia. Blood levels of catecholamines, cortisol, glucose, FFA, lactate, and electrolytes were measured. About 60% of the fish survived the experiment whereas the others died during the recovery period. Behavioral strategy appeared to be highly related to survival since nonsurviving fish displayed strenuous avoidance behavior involving burst type activity whereas surviving fish did not panic and remained quiet. These behavioral differences were associated with marked differences in plasma catecholamine levels, which were 4- to 5-fold higher in nonsurviving fish as compared to survivors whereas the cortisol response tends to be lower in nonsurviving fish. Plasma lactate levels in nonsurvivors were 4- to 5-fold higher as compared to survivors while a severe hyperkalemia developed during recovery indicating the loss of intracellular homeostasis. The individual differences in behavioral concepts and neuroendocrine activation observed in rainbow trout during stress show great similarity with the active and passive coping strategies distinguished in higher vertebrates and may be determinant for survival during hypoxia.

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Tilapia (Oreochromis mossambicus; teleostei) melanin-concentrating hormone gene-related peptide (tMgrp) was tested for tropic actions on adenocorticotropin hormone (ACTH) and alpha-melanocyte stimulating hormone (alpha-MSH) producing cells in the tilapia pituitary gland in vitro. Up to 100 microM synthetic tilapia Mgrp (tMgrp) had no effect on alpha-MSH release from tilapia neuro-intermediate lobes in a superfusion set up. However, at concentrations above 1 microM, tMgrp concentration dependently stimulated ACTH release from tilapia anterior lobes. This is the first evidence that Mgrp modulates ACTH release from teleost corticotropes, and this might implicate the peptide in the regulation of the pituitary-interrenal axis of fish.

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The melanin-concentrating hormone (MCH) precursor encodes MCH and a second peptide named neuropeptide EI (NEI) in mammals, neuropeptide EV (NEV) in salmonids and MCH gene-related peptide (Mgrp) in other fish. The primary structure of the putative Mgrp of the cichlid fish tilapia (Oreochromis mossambicus) appears to be very different from mammalian NEI and salmonid NEV. To investigate the processing and release of tilapia Mgrp (tMgrp), in the present study an antiserum was raised against synthetic tMgrp. By immunocytochemistry, tMgrp immunoreactivity was colocated with MCH immunoreactivity in the tilapia hypothalamus and pituitary. In addition, a tMgrp enzyme-linked immunosorbent assay in combination with reversed phase HPLC was used to demonstrate the presence of processed tMgrp in tilapia hypothalamus and pituitary. The release of tMgrp from neuro-intermediate lobes (NILs) of tilapia pituitaries was demonstrated after in vivo incubation of chopped NILs. Depolarizing concentrations of potassium significantly stimulated tMgrp release. Six weeks of adaptation of tilapia to white or black backgrounds had no effect on in vitro tMgrp release or on the tMgrp content of NIL and hypothalamus. Tilapia Mgrp, unlike MCH, had no effect on tilapia scale melanophores, nor did it modulate the melanin-concentrating effect of MCH. We conclude that tMgrp is processed from the MCH preprohormone, that it is released in vitro, and that the peptide has no direct role in the melanin concentration of fish scale melanophores. Therefore a neuroendocrine or neuromodulatory function is proposed for tMgrp.

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For some teleosts, a role has been established for melanin-concentrating hormone (MCH) background adaptation and stress response. In teleost fishes, prepro-MCH (ppMCH) mRNA is expressed in the hypothalamus, predominantly in neurons of the nucleus lateralis tuberis (NLT) and in scattered cells of the nucleus recessus lateralis (NRL). The response of mature tilapia to different environmental challenges was studied by assessing ppMCH mRNA levels in these two hypothalamic nuclei by quantitative dot blot analysis. Changes in background colour induced pronounced differences in ppMCH mRNA expression in the NLT, but not in the NRL. The NLT of tilapia adapted to a white background contained 2.5 to 3 times more ppMCH mRNA than the NLT of black-adapted fish. The NLT of fish kept on neutral background contained intermediate levels of ppMCH mRNA, which were significantly lower than the levels in white-adapted fish. Oral administration of dexamethasone lowered plasma cortisol concentrations, but had no effect on ppMCH mRNA levels in white- and black-adapted fish. In tilapia exposed to strongly acidified water (pH 3.5), plasma cortisol and ACThH concentrations were highly elevated, and plasma chloride concentrations considerably lower than in controls. These fish responded with a 70% rise in ppMCH mRNA levels in the NLT, which is most probably associated with a stress response evoked by inadequate osmoregulation. After exposure to a milder acidification (pH 4.0) or to seawater no significant changes in ppMCH mRNA levels occurred in either the NLT or the NRL, nor in plasma chloride, cortisol and ACTH levels. A specific increase of ppMCH mRNA levels in the NRL was observed in repeatedly disturbed tilapia.(ABSTRACT TRUNCATED AT 250 WORDS)

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Plasma levels of ACTH, alpha-MSH, and N-ac-beta-END, and in vitro interrenal ACTH sensitivity were investigated in rainbow trout (Oncorhynchus mykiss) stressed by confinement and in unstressed fish treated with exogenous cortisol. Within 3 hr after the onset of confinement, plasma cortisol and ACTH levels were significantly elevated above control values, while plasma alpha-MSH, but not N-ac-beta-END, levels were significantly decreased compared with those of unstressed fish. At 3 hr, sensitivity of the interrenal tissue to ACTH stimulation in vitro was reduced in stressed fish compared to that of unstressed controls. This hyposensitivity cannot be due to the intervention of alpha-MSH or N-ac-beta-END, because after 48 hr of confinement levels of both POMC-derived peptides were significantly lower than in controls, whereas interrenal tissue of stressed fish still responded significantly less to an ACTH challenge than tissue from control fish. Plasma cortisol and ACTH levels in confined fish at this time point were similar to those at 3 hr. Within 96 hr of the onset of confinement, plasma ACTH levels in stressed fish had returned to baseline levels. Plasma cortisol levels in stressed fish at 96 hr had also declined significantly, but were still higher than those in controls. The circulating cortisol level cannot be the regulatory factor responsible for the ACTH hyposensitivity observed after 3 and 48 hr of stress, because treatment of unstressed fish with exogenous cortisol (which resulted in elevated plasma cortisol and lower plasma ACTH and alpha-MSH levels compared to those of controls) did not induce a reduction in interrenal sensitivity to ACTH. It is suggested, instead, that these data support the contention that not only the initiation of the interrenal stress response, but also the habituation of the response, are regulated at the level of the hypothalamus via circulating ACTH levels.

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