Field Metabolic Rate in Two Species of Shrew-Tenrec, Microgale Dobsoni and M

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Field Metabolic Rate in Two Species of Shrew-Tenrec, Microgale Dobsoni and M Compo Biochem. Physiol. Vol. 107A, No.2, pp. 283-287, 1994 Copyright © 1994 Elsevier Science Ltd Pergamon Printed in Great Britain. All rights reserved 0300-9629/94 $6.00 + 0.00 Field metabolic rate in two species of shrew-tenrec, Microgale dobsoni and M. talazaci P. J. Stephenson, J. R. Speakman and P. A. Racey Department of Zoology, University of Aberdeen, Aberdeen, AB92TN, U.K. Doubly labelled water (DLW) was used to determine field metabolic rate (FMR) in the shrew-tenrecs Microgale dobsoni and M. talazaci. Measures were obtained on six animals in their natural habitat and on five individuals in captivity. Mean FMR for nonreproducing M. dobsoni (mean body mass 42.6 ± 1.7 g) was 77.1 ±3.2 kJ/d (CV = 53.7%, N = 4), 3.8 times resting metabolic rate (RMR). Mean FMR for nonreproducing M. talazaci (mean body mass 42.8 ± 4.9 g) was 66.5 ± 14.1 kJ/d (CV = 51.9%, N = 6),3.2 times RMR. FMR within each species was not significantly correlated with body mass. This may in part reflect the large variation among individuals combined with the small sample size. FMR in shrew-tenrecs was within the range of FMR found in similar sized rodents, although variation was greater in the tenrecs. The high variability of FMR within the Tenrecidae may be a result of variations in body temperature. FMR/RMR ratios for both species fell within the range determined for other small mammals. The present study therefore offers further evidence to support a relationship between FMR and RMR. Key words: Metabolic rate; Microgale dobsoni; M. talazaci; Doubly labelled water. Compo Biochem. Physiol. lO7A, 283-287, 1994. Introduction The doubly labelled water (DLW) techni­ Many species within the Tenrecidae (Mam­ que (Lifson et al., 1949, 1955; Lifson and malia: Insectivora) do not maintain constant McClintock, 1966) enables an estimate of CO 2 homeothermy (Eisenberg and Gould, 1970; production, and hence daily energy expenditure, Nicoll and Thompson, 1987; Stephenson, 1991). in free-living organisms (for reviews see Nagy, .Therefore, metabolic rate measured under stan­ 1980; Speakman and Racey, 1988; Bryant, 1989; dard conditions for BMR is commonly referred Speakman, 1990). Energy expenditure measured to as resting metabolic rate or RMR (Nicoll in this way is commonly referred to as field and Thompson, 1987). RMR in many species metabolic rate (FMR). It has been suggested of tenrec fluctuates independently of body that total daily energy expenditure in mammals mass due primarily to fluctuations in body is proportional to basal metabolic rate (BMR) temperature (Tb ) (Stephenson and Racey, (McNab, 1980; Drent and Daan, 1980; Peterson 1993a,b). Daily and seasonal variation in et al., 1990; Koteja, 1991), with FMR being set RMR and T, also occurs (Stephenson, 1991; at a maximum of about four times BMR. This Stephenson and Racey, in press c) so FMR is supported by analysis of residuals from curves would be expected to fluctuate widely between of metabolic rate against body mass which show and within individuals. a strong correlation between relative BMR and We investigated FMR in two species of relative FMR (Daan et al., in press). shrew-tenrec, Microgale dobsoni and M. tala­ zaci. Both species have RMR lower than pre­ dicted from body mass (Stephenson and Racey, Correspondence to: Peter J. Stephenson, Department of Zoology, University of Aberdeen, Tillydrone Avenue, 1993b). The only previous study to apply Aberdeen AB92TN, U.K. Fax: 224 272396. the DLW technique on a tenrec investigated the Received 24 April 1993; accepted 28 May 1993 energetics of reproduction in captive pygmy CPB(A) 107/2-8 283 284 P. J. Stephenson et at. hedgehog tenrecs, Echinops telfairi (Poppit, a variety of microhabitats such as herbaceous 1988). In the present study we aimed to study cover, tree roots and fallen logs. The plastic tenrecs in the wild in Madagascar. However, was pushed into the ground and tucked back the difficulties of retrapping study individuals below the leaf-litter root-mat layer to minimize meant most measures were taken on captive subterranean escape routes. The structure was animals or on semi-feral animals released into supported by trees and stakes of natural wood forest enclosures. We aimed to investigate the debris. Within the enclosures, tree trunks extent to which the field metabolic rates of and ground-lying branches were surrounded by M. dobsoni and M. talazaci are related to body plastic "collars" to block potential aerial run­ mass and RMR. ways. This was particularly important with M. talazaci which is semi-arboreal (Eisenberg Materials and Methods and Gould, 1970). Two nest boxes were placed in each enclosure. Tenrecs were introduced into M. dobsoni were captured from Reserve the enclosures via the nest boxes. Speciale (R.S.) Ambohitantely (l8°09'S, Animals were retrapped one or two nights 47°16'E) and M. talazaci were captured after initial injection. Lines of traps were laid from R.S. Analamazaotra (l8°28'S, 48°28'E) in the forest and up to 40 traps were placed in in Madagascar between January 1989 and each enclosure. The enclosure traps were February 1990. All tenrecs were trapped with checked every 2-3 hr during the night. Trap large Sherman mammal traps (H. B. Sherman lines outside the enclosures were checked each Traps Inc., Tallahasee, Florida, U.S.A.) baited morning at 0600-0800 hr. Recaptured animals with dried fish. The DLW technique was carried were reweighed and a second blood sample out on animals in their own habitat, although taken. All females used for DLW were taken measurements were also made on some individ­ back to Antananarivo and maintained in captiv­ uals held in captivity at the Pare Botanique et ity at Pare Tsimbazaza (see Stephenson and Zoologique de Tsimbazaza, Antananarivo. Racey, 1993b) to ascertain whether or not they Captured individuals were weighed, sexed had been pregnant during the study. and uniquely marked by ear-clipping. "Oxygen To measure background enrichment of in water (20.5 Atom Per cent Excess (APE), 180 and 2H, blood samples were taken from Yeda Research and Development Co. Ltd., individuals of the same sex, size and reproduc­ Rehovot, Israel) had previously been mixed tive condition as the study animals. Besides with deuterium (10 APE, Amersham Inter­ taking a blood sample from an animal before national, Little Chalfont, U.K.). The mass of injecting with DLW (which is impractical in DLW to be injected for each animal was esti­ small mammals), this is the most accurate way mated after Poppitt (1988) and was about 1% of of determining background isotope levels body mass. A 1ml syringe was filled with the (Speakman and Racey, 1987b). relevant volume of DLW (0.3-0.5 ml) and The 180 samples were prepared using the weighed to a precision of0.005 g using a White's guanidine technique (Speakman et al., 1990) torsion balance. The injection was administered and the 2H samples were prepared using intraperitoneally. uranium reduction (Wong and Klein, 1987). The syringe was reweighed immediately after Estimates of initial and final enrichments of 180 injection to determine mass of injectate. The and 2H were measured from duplicate samples study animal was then left undisturbed in a cloth using gas source stable isotope ratio mass spec­ bag for around 90 min to allow the isotopes to trometry (VG Isogas SIRA 9 and SIRA 10 mass reach equilibrium with body water (Speakman spectrometers). Estimates of CO2 production and Racey, 1987a). After this equilibrium period, were calculated using Equation 36 of Lifson an initial blood sample was taken from the tail and McClintock (1966) and converted to energy by removing the last 1-2 mm of skin with a sharp expenditure using the equation of Lusk (1976), scalpel. Blood was collected directly into 5 J..I.l assuming an RQ of 0.8. Mean values are pre­ capillary pipettes (Vitrex) which were sealed im­ sented in the text ± one standard error. mediately with a butane gas burner (Miniflam). The animal was then released. Results Since recapture rates for both species were low, enclosures were constructed at both study In the field, 13 individual M. dobsoni and 14 sites. These enclosures were barriers of trans­ individual M. talazaci were injected with DLW parent plastic sheet, 1-1.2 m high, erected and released. Of these, eight M. dobsoni (62%) around an area of forest (55 m2 at Ambohitan­ and four M. talazaci (29%) were recaught. tely and 20 m2 at Analamazaotra). Each enclo­ Of the 13 injected M. dobsoni released into sure was sited in the middle of known Microgale the enclosure at Ambohitantely, eight were habitat on relatively flat ground, incorporating recaught and of the five M. talazaci released Field metabolic rate in shrew-tenrecs 285 into the enclosure at Analamazaotra, two were to 20.1 kJjd. Therefore, mean FMR is 3.8 times recaught. Trap success was lower during the wet RMR. season (October-March) when animals were breeding and only two pregnant M. ta­ M. talazaci lazaci and one pregnant M. dobsoni were FMR in the field ranged from 32 to 80 kJjd trapped and injected with DLW. None of these (N = 3) compared with 40-124 kJjd (N = 3) in was recaptured. Sample loss during gas analyses captivity, but there was no significant difference meant that FMR was determined under natural in mean FMR (W = 9.0, P > 0.05). Captive conditions for only three M. dobsoni and three animals were not significantly heavier than M. talazaci. wild animals (W = 6.0, P > 0.05). Mean FMR In addition to field studies, six M. talazaci pooled across all non-reproducing adults (mean and six M.
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