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Substrate mobilization and hormonal changes in rainbow trout(Oncorhynchus mykiss, L.) and common carp (Cyprinu$ carpio, L.) during deep hypoxia and subsequent recovery Accepted: 7 May 1996 Abstract Common carp (at 20 °C) and rainbow trout (at 15 °C) were fitted with an indwelling cannula in the dorsal aorta. The fish were exposed to a controlled decline of water pO2 followed by 90 min deep hypoxia at 0.3 kPa (carp) or 4.8 kPa (trout). Thereafter, normoxic recovery was monitored in both species for 48 h. At regular intervals blood samples were analysed for glucose, lactate, free fatty acids, adrenaline, noradrenaline and cortisol. The oxygen restriction was maximal in both species and resulted in a significant increase of plasma lactate levels. In carp, adrenaline, noradrenaline and cortisol levels increased to 2, 50, and 753 ng.m1-1 respectively during anoxia, whereas in trout these hormones increased to 12, 8 and 735 ng" ml-1 respectively during hypoxia. In hypoxic trout, the plasma levels of glucose (3 mol'1-1) were increased modestly whereas levels of free fatty acids (0.25 mmol.1-1) were decreased to 0.15 mmol.1-1. In carp, however, a marked and prolonged hyperglycaemia (from 5 to 10 retool" 1-i) and a significant continuous depression of plasma levels of free fatty acids (from 0.4 to 0.2 mmol. 1-1) were observed indicating a difference in metabolic organization. It is suggested that hyperglycaemia is likely to be the result of hepatic glycogenolysis, stimulated by circulating catecholamines and a stimulation of gluconeogenesis by cortisol during recovery. The mechanism for the decline of plasma levels of free fatty acids is most

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Common carp (Cyprinus carpio L.), kept at 20 degrees C, were fitted with an indwelling PE-50 cannula in the dorsal aorta. Hormones dissolved in Ringer saline were arterially infused at a rate of 1 microgram.kg-1.min-1 for epinephrine (Epi), 2 micrograms.kg-1.min-1 for norepinephrine (NE), and 1.33 micrograms.kg-1.min-1 for insulin. INfusion of bovine insulin in carp resulted in a long lasting (24 h) decrease of plasma free fatty acids (FFA; -0.41 +/- 0.06 mM) and glucose levels (-3.14 +/- 0.25 mM) compared with preinfusion levels at t = 0. Both Epi and NE induced a marked hyperglycemia although Epi was more potent (+8.2 +/- 0.9 and +6.9 +/- 0.8 mM, respectively). Plasma FFA levels increased by 0.25 +/- 0.03 mM compared with preinfusion levels on Epi infusion. In contrast, during NE infusion, plasma FFA levels decreased significantly by -0.21 +/- 0.03 mM. Plasma insulin titers did not significantly change during infusion of NE or Epi. It is concluded that the ratio of NE to Epi is the major factor that determines the effect of catecholamines on plasma FFA levels in carp. These results may explain species-dependent different effects of hypoxia on FFA metabolism in fish.

This paper surveys the scientific basis for the current threshold approach for reproductive hazard and risk assessment. In some regulatory areas it was recently suggested to consider reproductive toxicants under the stringent linear extrapolation risk assessment paradigm that was developed for genotoxic carcinogens. First, the current risk assessment paradigm for genotoxic carcinogens is addressed, followed by an overview of reproductive toxicology and its threshold dose approach for hazard and risk assessment, the testing procedures for assessing the reproductive toxicity of chemicals, and the derivation of conclusions on their risk assessment and Classification, Labelling and Packaging (CLP). Relevant details of testing methodologies are discussed, such as exposure time windows, parameters determined, and the coverage of the entire reproductive cycle. In addition, the dose-response relationship is considered, illustrated with several examples. It is concluded that the current risk assessment methodology for genotoxic carcinogens is a debatable worst-case scenario and that for risk assessment of reproductive toxicants the threshold dose approach remains valid.