Juvenile rainbow trout, on 3% of body weight daily ration, were exposed to 0 (control) or 3 microg/L Cd (as Cd(NO3)2*4H2O) in moderately hard (140 mg/L as CaCO3), alkaline (95 mg/L as CaCO3, pH 8.0) water for 30 days. Particular attention focused on Cd burden in tissues (gills, liver, kidney, and whole body) and induction of metallothionein (MT) in gills, liver, and kidney during chronic Cd exposure. Mortality in Cd-exposed fish was minimal ( approximately 10%), and no growth effects occurred over the 30-day exposure. Cd accumulated in a time-dependent fashion to 9 times (gills), 3 times (liver), 20 times (kidney), 2 times (carcass), and 2 times (whole body) control levels by 30 days; absolute concentrations were in the order kidney > gill > liver > whole body > carcass. Tissue (gills, liver, and kidney) Zn and Cu burdens were not altered by chronic exposure to 3 microg/L Cd. MT concentrations in all tissues increased over the 30 days of Cd exposure, but the increases were much less than those of Cd on a molar binding site basis. Absolute MT concentrations were in the order liver > kidney > gill, but relative increases were greatest in kidney (fourfold), followed by gills (twofold) and liver (1.3-fold). MT levels were sufficient to bind all Cd in gill, liver, and kidney under control conditions, and after chronic Cd exposure remained sufficient in liver and kidney, but not in gills. Total metal levels (Cd + Zn + Cu) greatly exceeded MT binding capacity in all tissues under all conditions.
Thirty-six of the 70 species of bats known from Belize were recorded from the area around Lamanai, Orange Walk County: two in roosts and 34 in about 680 mist net hours that produced 560 captures. Day roosts used by 35 of the species were located using radio-tracking (Sturnira lilium, Platyrrhinus helleri, Centurio senex and Bauerus dubiaquercus) or general searching for roosts (Rhynchonycteris naso, Saccopteryx bilineata, Saccopteryx leptura, Dicli durus albus, Mimon bennettii, Micronycteris schmidtorum, Carollia brevicauda, Carollia perspicillata and Eptesicus furinalis). Data on the day roosts of 23 other species were determined from the literature. Most species reported from Lamanai (19) roosted in hollows, while others used foliage (6), tents (3), sheltered sites (2), crevices (2), open sites (1), and a few species used more than one type of day roost (hollows and crevices (1); hollows and foliage (1); hollows, foliage and tents (1)). The fauna consisted of 13 aerial foragers, 9 gleaners, 11 fruit/leaf eaters, one trawler, one flower-visitor and one blood-feeder. In day roost use and foraging behaviour, the Lamanai fauna did not differ significantly from that of Paracou, French Guiana, but both these locations differed from the bat fauna of Kruger National Park, South Africa, in foraging behaviour.
With the development of small implantable data loggers and externally attached temperature-sensitive radio transmitters, increasing attention is being paid to determining the thermoregulatory strategies of free-ranging birds and mammals. One of the constraints of such studies is that without a direct measure of metabolic rate, it is difficult to determine the significance of lowered body temperatures. We surveyed the literature and found that many different definitions have been used to discriminate torpor from normothermy. Many studies use arbitrary temperature thresholds without regard for the normothermic body temperature of the individuals or species involved. This variation makes comparison among studies difficult and means that ecologically and energetically significant small reductions in body temperature may be overlooked. We suggest that normothermic body temperature for each individual animal should be determined and that torpor be defined as occurring when the body temperature drops below that level. When individuals' active temperatures are not available, a species-specific value should be used. Of greater value, however, are the depth and duration of torpor bouts. We suggest several advantages of this definition over those used in the past.Résumé : Avec l'avènement d'appareils enregistreurs de données plus petits et de transmetteurs radio sensibles à la température portés à l'extérieur, il devient de plus en plus courant de déterminer les stratégies thermorégulatrices des oiseaux et des mammifères en nature. L'une des contraintes reliées à ce genre d'étude est qu'en l'absence d'une mesure directe du taux de métabolisme, il est difficile de déterminer l'importance d'une baisse de température corporelle. Dans la littérature, plusieurs définitions différentes sont utilisées pour distinguer la torpeur de la normothermie. Dans plusieurs études, les seuils de température sont arbitraires et la température normothermique du corps des individus ou des espèces n'est pas prise en considération. Cette variation rend difficiles les comparaisons entre les études et il se peut alors que des réductions de la température corporelle petites, mais significatives des points de vue écologique et énergétique, ne soient pas détectées. Nous croyons que la température normothermique du corps doit être mesurée chez tous les individus et nous proposons que la torpeur soit définie comme l'état qui prévaut quand la température du corps descend au-dessous de ce niveau. Lorsqu'il est impossible de mesurer la température de tous les individus, une valeur spécifique devrait être utilisée. Plus importantes encore sont la profondeur et la durée des périodes de torpeur. Nous indiquons ici plusieurs avantages de cette définition par comparaison à celles reconnues auparavant.[Traduit par la Rédaction] 1890 Notes
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