Energy requirements and metabolism of the Phillip's dikdik (Madoqua saltiana phillipsi)

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Abstract

Basal metabolic rates in mammals are mainly determined by body mass, but also by ecological factors. Some mammalian species inhabiting hot, dry environments were found to have lower metabolic rates compared to temperate species. We studied energy metabolism in Phillip's dikdik (Madoqua saltiana phillipsi), a small antelope inhabiting xeric shrubland habitats in the Eastern ‘horn’ of Africa, and compared results to literature data. We measured body mass (BM) changes and digestibility in 12 adults kept on different food intake levels to determine, by extrapolation to zero BM change, maintenance energy requirements (MEm) for metabolizable energy (ME). The MEm averaged at 404 ± 20 kJ ME kg BM 0.75 d 1. In addition we conducted 24 h-chamber respirometry with seven fed (non-fasted) individuals. Their mean metabolic rate as calculated from oxygen consumption was 403 ± 51 kJ kg BM 0.75 d 1, corroborating the results of the feeding experiments. Selecting the 20 lowest values of the respiration measurement period to estimate resting metabolic rate (RMR) resulted in a mean RMR of 244 ± 39 kJ kg BM 0.75 d 1, which was not significantly lower than the expected basal metabolic rate of 293 kJ kg BM 0.75 d 1. Therefore, resting metabolism was similar to the expected average basal metabolism of a mammal of this size, which suggests a comparatively low metabolic rate in dikdiks. Compared to literature data Phillip's dikdiks have a MEm similar to measurements reported for small domestic ruminants, but considerably lower than those reported for other wild ruminant species inhabiting temperate and cold climates.

Introduction

The basal metabolic rate (BMR) of mammals is mainly influenced by body mass (BM) (Kleiber, 1932, Brody, 1945, McNab, 2008), even though the exact scaling exponent of this allometric relationship has been the subject of intensive discussion (Glazier, 2005, Müller et al., 2012). However, it was repeatedly shown that there are other important factors besides BM influencing BMR such as habitat, climate, phylogeny, feeding habits or reproductive strategies, which explain some of the occasional deviation from the regression based on BM alone (e.g. McNab, 2008, Müller et al., 2012). Although Scholander et al. (1950) stated that animals do not adapt metabolic rate to climate, in particular McNab (2008) found that polar and cold-temperate habitats are inhabited by species with comparably high metabolic rates. Other studies demonstrated a lower metabolic rate in some mammals from hot environments when compared to species living in cold regions (as shown for an extensive dataset by Lovegrove, 2000, for canids in Careau et al., 2007, or small mammals in Lovegrove, 2003). Having a low metabolic rate in hot and/or arid environments can have several advantages: (1) it reduces endogenous heat load and thereby (2) reduces water loss for evaporative cooling (panting, sweating), which is the only physiological means for mammals to cool themselves (von Engelhardt and Breves, 2009); (3) it reduces energy requirements for maintenance, which is an important aspect in habitats that are not only characterized by drought but also where food can be limiting (Lovegrove, 2000). Overall, we can expect mammalian species living in hot, arid environments to have lower metabolic rates and energy requirements compared with species inhabiting regions with temperate climates.

In ruminants, dikdiks (Madoqua spp.), amongst the smallest extant species, have been labeled a miniature model for comparative physiological investigations (Maloiy et al., 1988). These animals inhabit the dry bush country of eastern and southern Africa, where conditions are semi-arid to arid, ambient temperatures are typically high, and surface water availability is low (Hendrichs and Hendrichs, 1971, Maloiy, 1973). During the dry season, dikdiks are additionally forced to cope with food scarcity (Manser and Brotherton, 1995). Several studies have already used dikdiks to study organismal adaptations, such as thermoregulation and water metabolism, to these harsh environmental conditions (Maloiy, 1973, Maskrey and Hoppe, 1979, Kamau and Maloiy, 1985, Kamau, 1988). However, results have been inconsistent across studies, and therefore generalizing conclusions are difficult to make. For instance, a mammal of dikdik size is expected to have a metabolic rate around 293 kJ kg BM 0.75 d 1 (based on the equation of Kleiber, 1961; see Methods), but values above and below this level have been reported. Maskrey and Hoppe (1979), using flow-through face masks, found a 20% higher-than-expected metabolic rate of 354 kJ kg BM 0.75 d 1 in Kirk's dikdik (Madoqua kirki), which they ascribed to the fact that subjects were not in a basal, post-absorptive condition during measurement. Another explanation could be that the high metabolic rates reflected a response to stress because the respiratory measurements had been carried out using face-masks. Applying chamber respirometry, Kamau and Maloiy (1981) found relatively low fasting metabolic rates of 154 to 218 kJ kg BM 0.75 d 1, and suggested that this was an adaptation to heat and aridity. Also high metabolic rates have been reported by Hoppe et al. (1983) (374 kJ kg BM 0.75 d 1 in fasting, and 406 ± 17 kJ kg BM 0.75 d 1 in fed, animals respectively), and low rates of 168 (dehydrated, fed individuals) to 223 kJ kg BM 0.75 d 1 (hydrated, fed individuals) were shown again by Kamau and Maloiy (1983). The most recent finding of 296 kJ kg BM 0.75 d 1 (Kamau, 1988) is close to the expected mammal average. This illustrates a huge between-study variation, which might at least partly be a consequence of the differences between the methods applied.

The disparity in published data for dikdik metabolic rates has in an inconsistent inclusion of this species in broader-scale comparative studies. Špála et al. (1987) used the results of Kamau and Maloiy (1981) in a comparative dataset to investigate energy requirements of domestic and captive wild ruminants. In that instance, the dikdik had an extraordinarily low value, which the authors had interpreted as a special adaptation to hot arid environments. In the comparative data collection of Lovegrove (2000), (which was later also used by Savage et al., 2004), an average value from the studies of Maskrey and Hoppe (1979) and Kamau and Maloiy (1982) was used, with a classification of the dikdik as a species inhabiting mesic rather than desert environments. Using this average, the dikdik's metabolism would be very close to the general mammalian average. In contrast, in the data collection of McNab (2008), only the data of Kamau (1988) were used, with a classification of the dikdik as inhabiting xeric environments. Although disparate categorization of a single species is unlikely to influence the overall result of these comparative studies which comprise data for large numbers of taxa – both Lovegrove (2000) and McNab (2008) – the question whether or not dikdiks show dry-region adaptations in their metabolic rate remains unsolved.

In order to clarify this controversy, we (i) evaluated the relationship between digestible energy intake and BM change as a means to estimate maintenance energy requirements (MEm), using data from a completed experiment in captive Phillip's dikdik (Hebel et al., 2011), and (ii) conducted individual gas exchange measurements in transportable respiratory chambers for the determination of metabolic rates. For comparison, we carried out a literature review on energy requirements in ruminants.

Section snippets

Materials and methods

The two experiments were conducted at Al Wabra Wildlife Preservation (AWWP), Qatar, with adult Phillip's dikdiks (Madoqua saltiana phillipsi) (hereafter referred to as dikdiks). Prior to the experiments, the animals were housed and fed according to AWWP guidelines for dikdik husbandry (Hammer, 2009). The animals were monitored constantly by a veterinarian, and subsequently released into their original pens after the experiments.

Results

In Experiment 1, out of the 12 individuals used in this study, 3 animals did not gain weight on any of the treatments used, i.e., not even when feed was offered ad libitum. For animal welfare reasons, the experimental period with an intake level of 70% had to be replaced by a second ad libitum session in two individuals. The regression equation determined based on the mixed model (BM change = 0.0016 (± 0.0004) × MEi  0.64 (± 0.13), n = 12) resulted in a MEm of 404 ± 20 kJ kg BM 0.75 d 1 for our subjects (

Discussion

Comparing the MEm values for dikdiks from the present study, as measured by feeding experiments and respiration measurements, with literature data for other selected species (Table 2) reveals that the dikdik is located at the lower end of the range in MEm covered by the ruminant species for which data exist. However, the dataset includes only few species that can be classified as inhabiting tropical environments (e.g., the mouse deer). This impedes the comparison among species. Additionally,

Acknowledgments

We thank H.E. Sheikh Saoud bin Mohammed bin Ali Al-Thani, the owner of AWWP for supporting this study. We are grateful to the whole team of AWWP for contributing to the realization of this study, especially Durga Bahadur Sarki. We also thank Qatar Museum authorities for their support. We are grateful to Andreas Mölich from Sable Systems Europe for his technical support, Heidrun Barleben for helping with the sample analyses, and Daryl Codron for editing the language. This study was part of

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    These authors contributed equally to this manuscript.

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    Present address: Institute for Veterinary Disease Control, Austrian Agency for Health and Food Safety—AGES, Innsbruck, Austria.

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    Present address: Naturschutz Tierpark Görlitz, Germany.

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    Present address: Department of Animal Sciences, University of Göttingen, Göttingen, Germany.

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