It is widely accepted that herbivores face nutritional challenges, including foods that vary in poorly digestible fibre (Milton 1979), plant-produced toxins (Rosenthal & Berenbaum 1991) and nutritionally imbalanced foods (Elser et al. 2000, 2007; Ritchie 2000). Such nutritional challenges may grow worse under ongoing climate change that shifts the range, timing and physiological conditions of forage plants (Tuanmu et al. 2012). In response to such challenges, animals have evolved behavioural, developmental and physiological adaptations that interact across time-scales to facilitate homoeostasis and maintain performance (Mayntz et al. 2005; Rothman et al. 2011). The science of nutritional ecology aims to understand the ways that these adaptations mediate the relationships between nutrient needs and ecological constraints (Raubenheimer, Simpson & Mayntz 2009). This helps to inform our understanding of the ecological and evolutionary processes that have shaped the diversity of animal foraging modes and to devise management strategies for endangered species and their habitats (Moore & Foley 2005; Raubenheimer, Simpson & Tait 2012).
An important response to variation in nutrient supply or demand (e.g. at different stages in the life cycle) is compensatory adjustment in foraging behaviour and physiological processing of nutrients (Raubenheimer, Simpson & Tait 2012). Foraging adjustments typically involve behaviours that balance the gain of several nutrients (e.g. usable energy, protein and amino acids, minerals), and physiological adjustments can involve changes in allocation to reproduction or other traits with particular nutritional demands. Animals that live in seasonal environments may be especially likely to adjust foraging and physiology to meet diverse nutritional challenges (Goldizen et al. 1988; Rubenstein & Wikelski 2003).
The giant panda (Ailuropoda melanoleuca) is an endangered, obligate herbivore that diverged early within an otherwise carnivorous clade (Qiu & Qi 1989; Wei et al. 2012; Zhao et al. 2013). Uniquely within the order Carnivora, pandas specialize (c. 99%) on various species of bamboo, resulting in a diet that is generally believed to be of poor quality due to low protein and high fibre and lignin contents, contributing to its low dry matter digestibility (Schaller et al. 1985; Hu et al. 1990; Wei et al. 1999; Zhu et al. 2011). Despite being exclusively herbivorous, the giant panda retains the simple stomach and short gastrointestinal tract typical of carnivores (Dierenfeld et al. 1982), and consequently needs to eat large amounts of poorly digestible foods (Hu et al. 1990). This high degree of specialization on large quantities of low quality food taken from a small number of plant species renders the giant panda vulnerable to extinction in the face of environmental change (Colles, Liow & Prinzing 2009). Further, its recently acquired herbivorous lifestyle provides an especially interesting opportunity for evaluating how shifts in herbivore behaviour allow a species to cope with food quality challenges involving the levels and balance of essential nutrients.
Previous studies have highlighted a number of interesting ecological and life-history characteristics that might be associated with the ability of panda populations to survive as bamboo specialists (Schaller et al. 1985; Pan et al. 2001). Nevertheless, these relationships remain poorly understood, largely because of the difficulty of obtaining intensive behavioural data for these secretive animals. Other bears give birth to unusually small, altricial young, a trait that has been associated with hibernation (Garshelis 2004). However, pandas do not hibernate and yet they have the shortest gestation period (3–5·5 months) and give birth to offspring that are the smallest of any bear species (Garshelis 2004; merely 0·1% of the mother's weight). As with other bears, pandas have an embryonic diapause, known as seasonal delayed implantation, in which the embryo remains suspended in the uterus in a state of arrested development until it attaches and resumes growth, sometimes months later (Schaller et al. 1985). While the adaptive significance of this remains uncertain (Thom, Johnson & MacDonald 2004), delayed implantation is believed to be an ecological adaptation to adjust the timing of mating and the rearing of offspring to different seasonal environments (Sandell 1990).
In this study, we used a combination of direct behavioural observations and individual-based characterization of food intake and egestion to assess the nutritional consequences of the seasonal food choices of pandas. We relate these choices to the timing of altitudinal migration and other major life-history events including seasonal mortality, mating, gestation, parturition and lactation. We focused our analysis on the mineral nutrients calcium and phosphorus, as well as nitrogen as a proxy for protein, because of the critical roles that these nutrients play in growth and reproduction of animals, including mammals (White 1993; McDowell 1996; Moen, Pastor & Cohen 1999; Sterner & Elser 2002). Importantly, mammalian requirements for calcium and phosphorus, principally for bone growth, are critically interdependent (Van Soest 1994; Underwood & Suttie 1999) and thus of special interest in the study of nutritional ecology of vertebrate herbivores. To examine the roles of these multiple dimensions of nutritional quality and their interdependencies, we organize our analysis using nutritional geometry, an approach for modelling the interactive effects of nutrients on animals (Raubenheimer 2011). Our objectives were i. to elucidate the relationships between the distinctive adaptations of these newly obligate herbivores, seasonal habitat choice, food selection and nutrient gain in the extreme nutritional environment to which they have become specialized and ii. to learn whether the respective foods and habitats of the giant pandas are interchangeable (alternative sources of the same resources), or complementary (provide different combinations of essential nutrients). The study thus provides fundamental insight into the nutritional ecology of a highly unusual and ecologically threatened herbivore, as well as critical information for the management and conservation of panda habitat.
Materials and methods
Study Site and Animals
This study was conducted in Foping Reserve, a key panda reserve, in the Qinling Mountains, China. The Qinling Mountains contain a high density of wild giant pandas with a population of 273 individuals (State Forestry Administration, China 2006). Two bamboo species are the main diet resource of the pandas there, wood bamboo (Bashania fargesii) and arrow bamboo (Fargesia qinlingensis), which grow at mean elevations of 1600 and 2400 m, respectively. These two bamboo species have different life histories. Wood bamboo (WB) produces shoots in May, and the shoots begin to sprout abundant new leaves in August. In contrast, arrow bamboo (AB) produces shoots in early June and its shoots sprout a limited number of new leaves in the following spring and considerably more new leaves in summer. The leaves of WB persist year-round, while the AB leaves drop off in winter.
With approval from the State Forestry Administration in China (2009-261), a total of six pandas, three adult females and males, respectively, were fitted with GPS/VHF collars (Lotek Wireless Inc., Ontario, Canada; Nie et al. 2012a,b; Zhang et al. 2014). This made it possible to conduct intensive behavioural observations and collect food samples, enabling us to determine individual-level seasonal food intake and obtain paired food–faecal samples for chemical analysis and assessment of relative digestive extraction efficiencies.
Observations of Foraging Behaviour and Sample Collection
Using the GPS collars, over 6 years, we tracked pandas from short distances (usually 10–20 m) to examine their seasonal pattern of food selection. Food and dung samples were collected in the four foraging seasons of 2009 and 2010. During this period, we also tracked pandas to conduct behavioural observations at intervals of 3–5 days for each individual, except when inclement weather prevented this. These observations enabled us to determine which bamboo species, tissues and ages were chosen by pandas. Paired food and fresh faeces samples were collected at each observed feeding patch during different foraging periods year-round. We defined a feeding patch as an area with a size of c. 300 × 300 m within which a panda was observed feeding for at least 24 h (because the gut passage time is usually around 10–12 h; Schaller et al. 1985). Bamboo leaf and shoot samples were collected according to the age of plants; that is, one- and multiyear old leaves, and new and old shoots, respectively. All food and faecal samples were coded by the feeding patch, dried in the field station, and the plant samples were sorted by different bamboo species and tissues. The dried plant and faecal samples were stored in zip-lock bags in the field for transport to laboratory.
Life Cycle and Mortality Data Collection
To examine the possible relationship between nutrition and reproduction strategy, we conducted a study of the reproductive ecology of giant pandas by tracking collared animals over 6 years from 2007 to 2012 (Nie et al. 2012a,b). We also analysed long-term (37 years) historical data of panda death and illness events in the wild from Foping Reserve records.
These data were used to explore the potential effect of food resource quality on the individual life span and population dynamics of this endangered species.
A total of 263 plant and faecal samples were collected in the field, including 66 shoots and 47 faecal samples during shoot foraging season, and 100 leaf and 50 faecal samples in leaf foraging season. All samples were ground to powder with a common multifunctional laboratory mill and oven-dried at 70 °C and then weighed before laboratory analyses. We used the micro-Kjeldahl method (Bremner 1996) to analyse N concentrations (% of dry mass). P contents (% of dry mass) were measured by the ammonium molybdate method after persulphate oxidation (Kuo 1996), standardized against known reference materials. Ca contents (% of dry mass) were determined using an atomic absorption spectrometer after hydrofluoric acid oxidation (Langmyhr & Thomassen 1973).
We used Right-angled Mixture Triangles (RMTs, Raubenheimer 2011) to explore the relationships among the proportional contents of nutrients in the foods and published estimates of nutrient requirements. To estimate digestive extraction efficiencies of Ca, P and N, we compared the proportional compositions of food samples with the associated faeces using RMTs. This method does not yield the absolute digestive efficiencies of separate nutrients, for which measures are needed of the absolute intake and excretion of each nutrient. Rather, by comparing the concentrations of nutrients in the food and matched faeces, we are able to establish the relative extraction efficiencies of the focal nutrients (Raubenheimer 2011). For example, if the concentration of P in the faeces was half that in the matched foods, we could not conclude that P was extracted with 50% efficiency, because we would not know the extent to which the change in P concentration from food to faeces was due to the extraction of other nutrients (i.e. changes in the denominator rather than numerator in the concentration ratio). However, if the Ca : P ratio in the food was twice the Ca : P ratio in the faeces, then, we could conclude that Ca was extracted with higher efficiency (by a factor of 2) than P. Since in this analysis we were interested in the relative extraction efficiencies of Ca, P and N, we chose to use an RMT model in which each nutrient was expressed as a percentage of the sum of the three nutrients [e.g. %Ca = Ca/(Ca + P + N) × 100] rather than as a percentage of the total sample mass (i.e. grams Ca/100 g sample). This enables the relative digestive efficiencies of all three nutrients to be compared in a single model, and also excludes from the denominator unaccounted components that might otherwise confound the comparison of relative extraction efficiencies (Raubenheimer 2011). We could then use as a baseline the null model in which all three nutrients are extracted from the food with equal efficiency, indicated in RMTs as the situation where the Ca–P–N ratio of faeces and the associated food is the same (i.e. the composition points for food and faeces are superimposed). Alternative outcomes would be indicated by the vectors of displacement of faeces composition relative to food; for example, if the Ca : P ratio in faeces is lower than in food, this indicates that Ca was extracted with higher efficiency than P.
We used t-tests to compare the concentrations and ratios of nutrients in the foods of pandas and to compare the ratios of nutrients in the foods with matched faecal samples to establish relative digestive efficiencies (as explained above). Levene's Test was used to test for equality of variances, and where the null hypothesis of equal variances was rejected, we applied a modified t-test that does not assume equal variances. A Kolmogorov–Smirnov Test was used to compare the observed monthly frequencies of mortality with the random null model. One-sample t-tests were used to compare dietary calcium: phosphorus ratios with the required ratios from the literature. All tests were performed using ibm spss v. 20 (IBM Corp., Armonk, NY, USA).
This is the first field study to use nutritional geometry to explore the relationship between the balance of essential nutrients, selection of foraging habitat, and the life cycle of a highly endangered herbivore species. Our data showed pandas experience marked seasonal foraging changes with four primary foraging periods corresponding to the annual phenology of the two bamboo species. The nutritional quality of the diet was heterogeneous through the year, both in terms of the absolute concentrations of N, P and Ca and the proportional balance of these nutrients. Seasonal diet switches corresponded with shifts in quantities of these key nutrients, as did the life cycle, reproduction and pattern of altitudinal migration. As we will discuss, the close correspondence between animal life-history events, shifting range, and forage quality suggest that nutritional balancing is a contributing component that maintains the population of this endangered species, an insight that may be crucial in its conservation as well as that of other endangered species that have narrow dietary ranges.
Our analysis showed that the N–P–Ca composition of diets varied with bamboo species, plant part and the age of the plant part. Age influenced primarily the concentration of nutrients, which declined as both leaves and shoots matured (Fig. 3a and b), most likely due to an increase in plant structural components such as cellulose, hemicellulose and lignin (Hu et al. 1990). In the absence of reliable measures of daily food intake (Rothman et al. 2011), which cannot readily be obtained for wild giant pandas in the field, it is difficult to interpret the significance of the concentration of a nutrient in foods in relation to the animal's requirement for that nutrient. Invariably, however, diet switches by pandas corresponded with a change to younger, more nutrient-rich alternatives, whether this involved a different plant part (e.g. arrow 1 in Fig. 3a and b) or species (e.g. arrow 2 in Fig. 3a and b). This preference for younger tissues could relate to their higher nutrient concentrations compared with older tissues in which nutrients are diluted by greater concentrations of structural components. Additionally, the biomechanical properties associated with plant structural components can also reduce the nutritional quality of foods (Clissold et al. 2009). Although we did not measure plant-produced allelochemicals, these might play a similar role (Launchbaugh, Provenza & Pfister 2001).
Nutrient concentrations also differed between species of bamboo, but these differences were contingent on the plant part. Specifically, the young shoots of wood bamboo had considerably higher N, P and Ca concentrations than the young arrow bamboo shoots, whereas the species difference was less marked and reversed for leaves (Fig. 3a and b). The greatest difference between plant parts, however, was in the balance of nutrients. Leaves had a higher N : P ratio (Fig. 3a) and a substantially higher Ca : P ratio (Fig. 3b) than did shoots, and this contrast applied for both bamboo species. Such differences in nutrient balance can be a significant parameter of food quality, because nutrient balance determines the ways that nutrients interact in their effects on consumers (Sterner & Elser 2002; Simpson & Raubenheimer 2012).
An important consideration in inferring the functional significance of seasonal diet switches in giant panda is therefore their implications for nutrient balance. Thus, the spring switch by the giant pandas in our study from leaves to shoots of wood bamboo corresponded with increased dietary N content, which could well be an important functional driver of the switch (White 1993). Significantly, dietary P content increased to a proportionally even greater extent than N, and consequently the dietary N : P ratio decreased. Since the N : P ratio of wood bamboo leaves was higher than the optimal range, the decrease corresponding to the switch to shoots brings the N : P ratio in the diet more in line with estimated requirements (the shaded area in Fig. 3a). The higher P concentrations in the shoots of wood bamboo do, however, have important consequences for giant pandas in relation to the dietary Ca : P ratio.
Dietary Ca : P ratios of 1 : 1–2 : 1 are recommended for mammals (Fig. 3b), with excesses of either nutrient interfering with the absorption and metabolism of the other (Robbins 2001). When the Ca : P ratio drops much below 1, P impedes absorption of the already limiting Ca, resulting in Ca resorption from bones and ultimately osteomalacia (softening of the bones) and associated diseases. In both human and animal studies, Ca : P ratios <0·5 have been associated with reduced bone mass density and compromised bone strength (Calvo & Tucker 2013). These effects can be particularly acute in relation to reproduction because of its increased calcium requirements for lactation and bone growth (Schulkin 2001). It is therefore noteworthy that the high levels of P in young wood bamboo shoots in our study resulted in Ca : P ratios of considerably <1 (0·2) . In contrast, Ca–P ratios in leaves were closer to the recommended range for mammals, being marginally above 2 (Fig. 3b). In general, Ca : P ratios higher than 2 (surplus Ca) are tolerated by herbivores to a greater extent than ratios <1 (surplus P) (Robbins 2001).
It is important to note that measures of Ca : P ratios in plant foods might not accurately represent the biologically effective Ca : P ratios, because a proportion of these elements might be bound in molecular complexes that render them unavailable (Suttle 2010). For example, phytic acid is an important storage form of P in many plant tissues (especially seeds) and is poorly digested by non-ruminant herbivores. However, if the relative excess of P in the panda diet was significantly influenced by unavailable P in this way, then, we would expect the faeces would be more highly P-enriched relative to Ca, but this was not the case. Rather, the faeces produced from bamboo shoots were enriched in Ca relative to P (i.e. the Ca : P ratio of faeces was greater than the Ca : P ratio of the shoots), and therefore, the postabsorptive Ca : P ratio associated with shoots was even lower than 0·2 (Fig. 4). The relatively high Ca levels in the faeces are consistent with the interfering effect of surplus P on Ca absorption discussed above. By contrast with shoots, the faeces associated with leaves were enriched in Ca but had statistically similar P contents to the leaves (Fig. 4). This selective egestion of Ca would bring the Ca : P ratio of leaves, which was marginally higher than 2, more closely in line with the recommended range.
Our nutritional analysis therefore implies that, when pandas switch from a diet of old leaves to shoots of wood bamboo at around the time of mating, they shift from a diet that is low in both N and P with a N : P ratio that exceeds the maximum recommended for mammals to a diet that is higher in both nutrients and has an N : P ratio within the recommended range (Fig. 3a). With the subsequent switch to arrow bamboo shoots, the dietary concentrations of both N and P were reduced but the N : P ratio was very close to the centre of the expected N : P range (c. 6·75, Fig. 3a). These high shoot N and P contents likely help support construction of the placenta and the growing embryo during foetal development. During this period, however, the dietary Ca : P ratio was considerably lower than considered necessary to support reproduction in mammals and was only restored with the subsequent switch to arrow bamboo leaves (Figs 2 and 3b).
These dynamics lead us to suggest that perhaps delayed implantation provides a means for pandas to postpone the Ca investment in lactation and bone growth, synchronizing these more closely with a leaf-based diet that can support them. On the other hand, the relatively low levels of both N and P, and the high N : P ratios in the autumn and winter diet, present additional challenges for panda reproduction. Specifically, both N and P are required for tissue growth, and there would be obvious fitness penalties for pandas that could not acquire these in sufficient quantities for reproduction. An interesting possibility is that this could be related to the evolutionary maintenance and enhancement of the short gestation period of pandas, and the extremely small size of the offspring at birth (Garshelis 2004). Giving birth to altricial young would ease the burden on the mother for acquiring limiting nutrients, by enabling the offspring to start independent feeding (i.e. weaning) earlier. Having both mother and offspring eating to meet their own respective nutrient needs would allow the pair to process bamboo and acquire limiting nutrients at a greater rate than if the burden fell on the mother alone. Barclay (1994) used similar reasoning to argue that the long development time for flight, which delays independent foraging in flying vertebrates (bats and birds), might impose constraints on Ca acquisition for bone growth and explain why these animals generally have small litters. The peak in panda mortality in March and April is also consistent with an interpretation that the extended low quality of the winter diet of leaves is nutritionally stressful, highlighting the need for both mother and offspring to forage for limiting nutrients.
In summary, our analysis has shown that young shoots of wood bamboo were high in P and N but had a Ca : P ratio markedly lower than is considered necessary to support bone growth in mammals. In June, the levels of P, Ca and N dropped in the maturing shoots of wood bamboo, whereupon the pandas migrated to higher elevation. This allowed them to switch to arrow bamboo shoots, which had higher levels of P, N and Ca but again a sub-optimally low Ca : P ratio. By early August, during the late stages of gestation, nutrient levels in arrow bamboo shoots had dropped and the pandas switched to feeding on the leaves of the same species. These had higher nutrient levels, in particular Ca, a more favourable Ca : P ratio, and a better Ca : P absorption profile than bamboo shoots. In August, females returned to the lower elevation feeding sites where birthing coincided with the availability of young wood bamboo leaves, with high nutrient content and a high Ca : P ratio. However, as wood bamboo leaves aged through the winter, their P content decreased, reaching their lowest level in the period that coincides with the highest historical mortality rate. At that point, the pandas again switched to young wood bamboo shoots once they became available.
Overall, our results also suggest that the two bamboo species are nutritionally interchangeable but that different plant parts (shoots and leaves) are not. Rather, the shoots and leaves are nutritionally complementary resources, with shoots providing primarily N and P, but deficient in Ca, which is provided by the leaves. Both species of bamboo are, nonetheless, critical for the pandas, because their asynchronous phenology, coupled with seasonal altitudinal migration, enables the pandas to complete their life cycle on this low diversity and highly specialized diet. Our insights into the phenological dynamics of panda nutrition have important implications for managing the conservation of this charismatic species in the face of climate change. Tuanmu et al. (2012) recently modelled likely future distributions of wood and arrow bamboo in the light of several IPCC climate projections for the Qinling Mountain region (our study area). They noted strong potential for range contraction and elevation shifts in these species, changes that are likely to lead to phenological mismatches between the timing of panda life cycle events and the nutritional suitability of bamboo. Such possibilities highlight the need for a systems-approach to panda conservation, in which pandas, both species of their food plants, and their respective habitats, both current and projected, are all afforded protection. More broadly, this work gives us a new insight into animal nutritional ecology of potential benefit to further research in the field of animal ecology and conservation biology, especially for species that face serious nutritional challenges due to accelerating environmental change.