Abstract
The ecoevolutionary dynamics of species are fundamentally linked to the energetic constraints of their constituent individuals. Of particular importance is the interplay between reproduction and the dynamics of starvation and recovery. To elucidate this interplay, here we introduce a nutritional statestructured model that incorporates two classes of consumers: nutritionally replete, reproducing consumers, and undernourished, nonreproducing consumers. We obtain strong constraints on starvation and recovery rates by deriving allometric scaling relationships and find that population dynamics are typically driven to a steady state. Moreover, these rates fall within a “refuge” in parameter space, where the probability of population extinction is minimized. We also show that our model provides a natural framework to predict steady state population abundances known as Damuth's law, and maximum mammalian body size. By determining the relative stability of an otherwise homogeneous population to a competing population with altered percent body fat, this framework provides a principled mechanism for a selective driver of Cope’s rule.
Introduction
The behavioral ecology of all organisms is influenced by their energetic states, which directly impacts how they invest reserves in uncertain environments. Such behaviors are generally manifested as tradeoffs between investing in somatic maintenance or allocating energy toward reproduction^{1,2,3}. The timing of these behaviors responds to selective pressure, as the choice of the investment impacts future fitness^{4,5}. The influence of resource limitation on an organism’s ability to maintain its nutritional stores may lead to repeated delays or shifts in reproduction over the course of an organism’s life.
The balance between (a) somatic growth and maintenance, and (b) reproduction depends on resource availability^{6}. For example, reindeer invest less in calves born after harsh winters (when the mother’s energetic state is depleted) than in calves born after moderate winters^{7}. Many bird species invest differently in broods during periods of resource scarcity^{8,9}, sometimes delaying or even foregoing reproduction for a breeding season^{1,10,11}. Even freshwater and marine zooplankton have been observed to avoid reproduction under nutritional stress^{12}, and those that do reproduce have lower survival rates^{2}. Organisms may also separate maintenance and growth from reproduction over space and time: many salmonids, birds, and some mammals return to migratory breeding grounds to reproduce after one or multiple seasons in resourcerich environments where they accumulate reserves^{13,14,15}.
Physiology also plays an important role in regulating reproductive expenditures during periods of resource limitation. Many mammals (47 species in ten families) exhibit delayed implantation, whereby females postpone fetal development until nutritional reserves can be accumulated^{16,17}. Many other species (including humans) suffer irregular menstrual cycling and higher abortion rates during periods of nutritional stress^{18,19}. In the extreme case of unicellular organisms, nutrition directly controls growth to a reproductive state^{3,20}. The existence of so many independently evolved mechanisms across such a diverse suite of organisms highlights the nearuniversality of the fundamental tradeoff between somatic and reproductive investment.
Including individual energetic dynamics^{21} in a populationlevel framework^{21,22} is challenging^{23}. A common simplifying approach is the classic Lotka–Volterra (LV) model, which assumes that consumer population growth rate depends linearly on resource density^{24}. Here, we introduce an alternative approach—the nutritional statestructured model (NSM)—that accounts for resource limitation via explicit starvation. In contrast to the LV model, the NSM incorporates two consumer states: hungry and full, with only the former susceptible to mortality and only the latter possessing sufficient energetic reserves to reproduce. Additionally, we incorporate allometrically derived constraints on the timescales for reproduction^{3}, starvation, and recovery. Our model makes several basic predictions: (i) the dynamics are typically driven to a refuge far from cyclic behavior and extinction risk, (ii) the steadystate conditions of the NSM accurately predict the measured biomass densities for mammals described by Damuth’s law^{25,26,27,28}, (iii) there is an allometrically constrained upper bound for mammalian body size, and (iv) the NSM provides a selective mechanism for the evolution of larger body size, known as Cope’s rule^{29,30,31,32}.
Results
Nutritional statestructured model
We begin by defining the nutritional statestructured population model, where the consumer population is partitioned into two states: (a) an energetically replete (full) state F, where the consumer reproduces at a constant rate λ and does not die from starvation, and (b) an energetically deficient (hungry) state H, where the consumer does not reproduce but dies by starvation at rate μ. The dynamics of the underlying resource R are governed by logistic growth with an intrinsic growth rate α and a carrying capacity C. The rate at which consumers transition between states and consume resources is dependent on their number, the abundance of resources, the efficiency of converting resources into metabolism, and how that metabolism is partitioned between maintenance and growth purposes. We provide a physiologically and energetically mechanistic model for each of these dynamics and constants (Methods), and show that the system produces a simple nondimensional form that we describe below.
Consumers transition from the full state F to the hungry state H at a rate σ—the starvation rate—and also in proportion to the absence of resources (1−R) (the maximum resource density has been nondimensionalized to 1; see Methods). Conversely, consumers recover from state H to state F at rate ξρ and in proportion to R, where ξ represents a ratio between maximal resource consumption and the carrying capacity of the resource. The resources that are eaten by hungry consumers (at rate ρR+δ) account for their somatic growth (ρR) and maintenance (δ). Full consumers eat resources at a constant rate β that accounts for maximal maintenance and somatic growth (see Methods for mechanistic derivations of these rates from resource energetics). The NSM represents an ecologically motivated fundamental extension of the idealized starving random walk model of foraging, which focuses on resource depletion, to include reproduction and resource replenishment^{33,34,35}, and is a more general formulation than previous models that incorporate starvation^{36,37}.
In the meanfield approximation, in which the consumers and resources are perfectly mixed, their densities are governed by the rate equations
This system of nondimensional equations follows from a set of firstprinciple relationships for resource consumption and growth (see Methods for a full derivation and the dimensional form). Notice that the total consumer density F+H follows \(\dot F + \dot H = \lambda F  \mu H\). This resembles the equation of motion for the predator density in the LV model^{38}, except that the resource density does not appear in the growth term. The rate of reproduction is independent of resource density because the full consumer partitions a constant amount of energy toward reproduction, whereas a hungry consumer partitions no energy toward reproduction. Similarly, the consumer maintenance terms (δH and βF) are also independent of resource density because they represent a minimal energetic requirement for consumers in the H and F state, respectively.
Steady states of the NSM
From the single internal fixed point (Eq. 5, see Methods), an obvious constraint on the NSM is that the reproduction rate λ must be less than the starvation rate σ, so that the consumer and resource densities are positive. The condition σ = λ represents a transcritical (TC) bifurcation^{39} that demarcates a physical from an unphysical (negative steadystate densities) regime. The biological implication of the constraint λ < σ has a simple interpretation—the rate at which a macroscopic organism loses mass due to lack of resources is generally much faster than the rate of reproduction. As we will discuss below, this inequality is also a natural consequence of allometric constraints for organisms within empirically observed body size ranges.
In the physical regime of λ < σ, the fixed point (Eq. 5) may either be a stable node or a limit cycle (Fig. 1). In continuoustime systems, a limit cycle arises when a pair of complex conjugate eigenvalues crosses the imaginary axis to attain positive real parts^{40}. This Hopf bifurcation is defined by Det(S) = 0, where S is the Sylvester matrix, which is composed of the coefficients of the characteristic polynomial of the Jacobian matrix^{41}. As the system parameters are tuned to be within the stable regime, but close to the Hopf bifurcation, the amplitude of the transient cycles becomes large. Given that ecological systems are constantly being perturbed^{42}, the onset of transient cycles, even though they decay with time in the meanfield description, can increase extinction risk^{43,44,45}.
When the starvation rate σ >> λ, a substantial fraction of the consumers is driven to the hungry nonreproducing state. Because reproduction is inhibited, there is a low steadystate consumer density and a high steadystate resource density. However, if σ/λ→1 from above, the population is overloaded with energetically replete (reproducing) individuals, thereby promoting transient oscillations between the consumer and resource densities (Fig. 1). If the starvation rate is low enough that the Hopf bifurcation is crossed, these oscillations become stable. This threshold occurs at higher values of the starvation rate as the recovery rate ρ increases, such that the range of parameter space giving rise to cyclic dynamics also increases with higher recovery rates.
The allometry of extinction risk
While there are no a priori constraints on the parameters in the NSM, we expect that each species should be restricted to a distinct portion of the parameter space. We use allometric scaling relations to constrain the covariation of rates in a principled and biologically meaningful manner (Methods). Allometric scaling relations highlight common constraints and average trends across large ranges in body size and species diversity. Many of these relations can be derived from a small set of assumptions. In Methods, we describe our framework to determine the covariation of timescales and rates across a range of body sizes for each of the key parameters of our model (cf. ref. ^{46}).
Nearly all of the rates described in the NSM are determined by consumer metabolism, which can be used to describe a variety of organismal features^{47}. We derive, from first principles, the relationships for the rates of reproduction, starvation, recovery, and mortality as a function of an organism’s body size and metabolic rate (Methods). Because we aim to explore the starvationrecovery dynamics as a function of an organism’s body mass M, we parameterize these rates in terms of the percent gain and loss of the asymptotic (maximum) body mass, εM, where different values of ε define different states of the consumer (Fig. 2; see Methods for derivations of allometrically constrained rate equations). Although the rate equations (1) are general and can in principle be used to explore the starvationrecovery dynamics for most organisms, here, we focus on allometric relationships for terrestrialbound lowertrophiclevel endotherms (Table 1), specifically herbivorous mammals, which range from a minimum of M ≈ 1 g (the Etruscan shrew Suncus etruscus) to a maximum of M ≈ 10^{7} g (the early Oligocene Indricotheriinae and the Miocene Deinotheriinae). Investigating other classes of organisms would simply involve altering the metabolic exponents and scalings associated with ε. Moreover, we emphasize that our allometric equations describe mean relationships and do not account for the (sometimes considerable) variance associated with individual species. We note that including additional allometrically scaled mortality terms to both F and H does not change the form of our model nor impact our quantitative findings (Supplementary Note 1).
As the allometric derivations of the NSM rate laws reveal (Methods), starvation and recovery rates are not independent parameters, and the biologically relevant portion of the phase space shown in Fig. 1 is constrained via covarying parameters. Given the parameters of terrestrial endotherms, we find that the starvation rate σ and the recovery rate ρ are constrained to lie within a small region of potential values for the known range of body size M. Indeed, starvation and recovery rates across all values of M fall squarely in the steadystate region at some distance from the Hopf bifurcation. This suggests that cyclic population dynamics should be rare, particularly in resourcelimited environments.
Higher rates of starvation result in a larger flux of the population to the hungry state. In this state, reproduction is absent, thus increasing the likelihood of extinction. From the perspective of population survival, it is the rate of starvation relative to the rate of recovery that determines the longterm dynamics of the various species (Fig. 1). We therefore examine the competing effects of cyclic dynamics vs. changes in steadystate density on extinction risk, both as functions of σ and ρ. To this end, we computed the probability of extinction, where we define extinction as a population trajectory falling below onefifth of the allometrically constrained steady state at any time between t = 10^{8} and t = 10^{10}. This procedure was repeated for 50 replicates of the continuoustime system shown in Eq. 1 for organisms with mass ranging from 10^{2} to 10^{6} g. In each replicate, the initial densities were chosen to be (XF^{*}, XH^{*}, R^{*}), with X a random variable uniformly distributed in [0, 2]. By allowing the rate of starvation to vary, we assessed extinction risk across a range of values for σ and ρ between ca. 10^{−8} and 10^{−3}. Higher rates of extinction correspond to both large σ if ρ is small, and large ρ if σ is small. In the former case, increased extinction risk arises because of the decrease in the steadystate consumer population density (Figs. 1, 3). In the latter case, the increased extinction risk results from higheramplitude transient cycles as the system nears the Hopf bifurcation (Fig. 3). This interplay creates an “extinction refuge”, such that for a constrained range of σ and ρ, extinction probabilities are minimized.
We find that the allometrically constrained values of σ and ρ, each representing different trajectories along the ontogenetic curve (Fig. 2), fall squarely within the extinction refuge across a range of Μ (Fig. 3a, b, white points). These values are close enough to the Hopf bifurcation to avoid low steadystate densities, yet distant enough to avoid largeamplitude transient cycles. Allometric values of σ and ρ fall within this relatively small window, which supports the possibility that a selective mechanism has constrained the physiological conditions driving starvation and recovery rates within populations. Such a mechanism would select for organism physiology that generates appropriate σ and ρ values that minimize extinction risk. This selection could occur via the tuning of body fat percentages, metabolic rates, and/or biomass maintenance efficiencies. We also find that as body size increases, the size of the low extinctionrisk parameter space shrinks (Fig. 3b), suggesting that the population dynamics for larger organisms are more sensitive to variability in physiological rates. This finding is in accordance with, and may serve as contributing support for, observations of increased extinction risk among larger mammals^{48}.
Damuth’s law and body size limits
The NSM correctly predicts that smaller species have larger steadystate population densities (Fig. 4). Similar predictions have been made for carnivore populations using alternative consumerresource models^{49}. Moreover, we show that the NSM provides independent theoretical support for Damuth’s law^{25,26,27,28}. Damuth’s law shows that species abundances, Ν^{*}, follow Ν^{*} = 0.01Μ^{−0.78} (g m^{−2}). Figure 4 shows that both F^{*} and Η^{*} scale as M^{−η}, with η ≈ 3/4, over a wide range of organismal sizes and that F^{*}+ Η^{*} closely matches the best fit to Damuth’s data. Remarkably, this result illustrates that the steadystate values of the NSM combined with the derived timescales naturally give rise to Damuth’s law. While the initial metabolic studies supporting Damuth’s law provide arguments for the value of the exponent^{25,26} (Supplementary Note 2), our model predicts not only the exponent but also the normalization constant dependencies by explicitly including the resource dynamics and the parameters that determine growth and consumption. These predictions are complementary to recent work that also predicts the exponent and normalization constant of density relationships from the detailed allometries of reproduction, capture area, conversion efficiency, and mortality within predator–prey dynamic models^{49,50}. It should be noted that density relationships of individual clades follow a more shallow scaling relationship than that predicted by Damuth’s law^{28}. In the context of our model, this finding suggests that future work may be able to anticipate these shifts by accounting for differences in the physiological parameters associated with each clade.
With respect to predicted steadystate densities, the population sizes of both F and H go to zero at a finite body size, where the steadystate resources also vanish (Fig. 4). This behavior is governed by the body size at which f_{0}M^{γ−1}+u_{0}M^{ζ−1} = 1 (Supplementary Note 3) that causes the death rate to vanish, μ = 0, and corresponds to (F^{*}, H^{*}, R^{*}) = (0, 0, 0). Just before this point H^{*} becomes large, in accordance with the asymptotic behavior in Fig. 4. This point predicts an upper bound on mammalian body size at M_{max} = 6.54 × 10^{7} g. Moreover, M_{max}, which is entirely determined by the populationlevel consequences of energetic constraints, is within an order of magnitude of the maximum body size observed in the North American mammalian fossil record^{29}, as well as the mass predicted from an evolutionary model of body size evolution^{30}. We emphasize that the asymptotic behavior and predicted upper bound depend only on the scaling of body composition and are independent of the resource parameters. The prediction of an asymptotic limit on mammalian size parallels work on microbial life where an upper and lower bound on bacterial size, and an upper bound on singlecell eukaryotic size, is predicted from similar growth and energetic scaling relationships^{3,51}. It has also been shown that models that incorporate the allometry of hunting and resting combined with foraging time predicts a maximum carnivore size between 7 × 10^{5} and 1.1 × 10^{6} g^{52,53}. Similarly, the maximum body size within a particular lineage has been shown to scale with the metabolic normalization constant^{54}. This complementary approach is based on the balance between growth and mortality, and suggests that future connections between the scaling of fat and muscle mass should systematically be connected with B_{0} when comparing lineages.
A mechanism for Cope’s rule
Metabolite transport constraints are widely thought to place limits on biological scaling^{47,55} and thereby lead to specific predictions on the minimum possible body size for organisms^{56}. Above this bound, a number of energetic and evolutionary mechanisms have been explored to assess the costs and benefits associated with larger body masses, particularly for mammals. One important such example is the “fasting endurance hypothesis”, which contends that larger body size, with consequent lower metabolic rates and increased ability to maintain more endogenous energetic reserves, may buffer organisms against environmental fluctuations in resource availability^{57}. Over evolutionary time, terrestrial mammalian lineages show a significant trend toward larger body size—Cope’s rule^{29,30,31,32}. It is thought that withinlineage drivers generate selection toward an optimal upper bound of roughly 10^{7} g^{29}, a value that is likely limited by higher extinction risk for large taxa over longer timescales^{30}. These trends are thought to be driven by a combination of climate change and niche availability^{32}; however, the underpinning energetic costs and benefits of larger body sizes, and how they influence dynamics over ecological timescales, have not been explored.
The NSM predicts that the steadystate resource density R^{*} decreases with increasing body size of the consumer population (Fig. 4, inset), and classic resource competition theory predicts that the species surviving on the lowest resource abundance will outcompete others^{58,59,60}. Thus, the combined NSM steadystate dynamics and allometric timescales (Eq. 7) predict that larger mammals have an intrinsic competitive advantage given a common resource.
However, the above resource relationships do not offer a mechanism for how body size is selected. We directly assess competitive outcome between two closely related species: a resident species of mass M, and a competing species (denoted by ′) where individuals have a different proportion of body fat such that M′ = M(1+χ). For χ < 0, the competing individuals have fewer metabolic reserves than the resident species and vice versa for χ > 0. For the allowable values of χ (Methods), the mass of the competitor M′ should exceed the minimal amount of body fat, 1 + χ > ε_{ σ }, and the adjusted time to reproduce must be positive, which, given Eq. 7, implies that \(1  \varepsilon _{\mathrm{\lambda }}^{1  \eta }\left( {1 + \chi } \right)^{1  \eta } \, > \, 0\). These conditions imply that \(\chi \in (  f_0M^{\gamma  1},1/\varepsilon _{\mathrm{\lambda }}  1)\) where the upper bound approximately equals 0.05 and the lower bound is massdependent. The modified mass of the competitor leads to altered rates of starvation σ(M′), recovery ρ(M′), and the maintenance of both starving δ(M′) and full consumers β(M′) (see Methods for derivations of competitor rates). Importantly, ε_{ σ }, which determines the point along the growth curve that defines the body composition of starved foragers, is assumed to remain unchanged for the competing population.
To assess the susceptibility of the resident species to competitive exclusion, we determine which consumer pushes the steadystate resource density R^{*} to lower values for a given value of χ, with the expectation that a population capable of surviving on lowerresource densities has a competitive advantage^{58}. We find that for M ≤ 1.748 × 10^{7} g, having additional body fat (χ > 0) results in a lower steadystate resource density (R′^{*} < R^{*}), such that the competitor has an intrinsic advantage over the resident species (Fig. 5). However, for M > 1.748 × 10^{7} g, leaner individuals (χ < 0) have lowerresource steadystate densities.
The observed switch in susceptibility as a function of χ at M_{opt} = 1.748 × 10^{7} g thus serves as an attractor, such that the NSM predicts organismal mass to increase if M < M_{opt} and decrease if M > M_{opt}. This value is close to but smaller than the asymptotic upper bound for terrestrial mammal body size predicted by the NSM, and is remarkably close to independent estimates of the largest land mammals, the early Oligocene Indricotherium at ≈1.5 × 10^{7} g and the late Miocene Deinotherium at ≈1.74 × 10^{7} g^{31}. Additionally, our calculation of M_{opt} as a function of massdependent physiological rates is similar to theoretical estimates of maximum body size^{30}, and provides independent theoretical support for the observation of a “maximum body size attractor” explored by Alroy^{29}.
An optimal size for mammals at intermediate body mass was predicted by Brown et al.^{37} based on reproductive maximization and the transition between hungry and full individuals. By coupling the NSM to resource dynamics as well as introducing an explicit treatment of storage, we show that species with larger body masses have an inherent competitive advantage for size classes up to M_{opt} = 1.748 × 10^{7} based on resource competition. Moreover, the mass distributions in ref. ^{37} show that intermediate mammal sizes have the greatest species diversity, in contrast to our efforts, which consider total biomass and predict a much larger M_{opt}. Compellingly, recent work shows that many communities can be dominated by the biomass of the large^{61}. While the state of the environment as well as the competitive landscape will determine whether specific body sizes are selected for or against^{32}, we propose that the dynamics of starvation and recovery described in the NSM provide a general selective mechanism for the evolution of larger body size among terrestrial mammals.
Discussion
The energetics associated with somatic maintenance, growth, and reproduction are important elements that influence the dynamics of all populations^{10}. The NSM incorporates the dynamics of starvation and recovery that are expected to occur in resourcelimited environments. We found that incorporating allometrically determined rates into the NSM predicts that (i) extinction risk is minimized, (ii) the derived steady states quantitatively reproduce Damuth’s law, and (iii) the selective mechanism for the evolution of larger body sizes agrees with Cope’s rule. The NSM offers a means by which the dynamic consequences of energetic constraints can be assessed using macroscale interactions between and among species.
Methods
Mechanisms of starvation and recovery
To understand the dynamics of starvation, recovery, reproduction, and resource competition, our framework partitions consumers into two classes: (a) a full class that is able to reproduce and, (b) a hungry class that experiences mortality at a given rate and is unable to reproduce. For the dynamics of growth, reproduction, and resource consumption, past efforts have combined the overall metabolic rate, as dictated by body size, with a growth rate that is dependent on resource abundance and, in turn, dictates resource consumption (see refs. ^{3,62} for a brief review of this perspective). This approach has been used to understand a range of phenomena including a derivation of ontogenetic growth curves from a partitioning of metabolism into maintenance and biosynthesis^{3,63,64,65} and predictions for the steadystate resource abundance in communities of cells^{62}. Here, we leverage these mechanisms, combined with several additional concepts, to define our NSM.
We consider the following generalized set of explicit dynamics for starvation, recovery, reproduction, and resource growth and consumption
where each term has a mechanistic meaning that we detail below (we will denote the dimensional equations with the subscript _{d} before introducing the nondimensional form that is presented in the main text). In the above equations, Y represents the yield coefficient^{66,67} that is the quantity of resources required to build a unit of organism (gram of mammal produced per gram of resource consumed) and P is the specific maintenance rate of resource consumption (g resource · s^{−1} · g organism^{−1}). If we pick F_{d} and H_{d} to have units of (g organisms · m^{−2}), then all of the terms of \(\dot R_{\mathrm{d}}\), such as \(\frac{{\rho \left( {R_{\mathrm{d}}} \right)}}{Y}H_{\mathrm{d}}\), have units of (g resource · m^{−2} · s^{−1}), the typical units of net primary productivity (NPP), a natural choice for \(\dot R_{\mathrm{d}}\). This choice also gives R_{d} as (g m^{−2}) that is also a natural unit and is simply the biomass density. In these units, α (s^{−1}) is the specific growth rate of R_{d}, C is the carrying capacity, or maximum density, of R_{d} in a particular environment, and k is the halfsaturation constant (half the density of resources that would lead to maximum growth).
We can formally nondimensionalize this system by the rescaling of F = fF_{d}, H = fH_{d}, R = qR_{d}, and t = st_{d}, in which case our system of equations becomes
If we make the natural choice of s = 1, q = 1/C, and f = 1/Y_{H}k, then we are left with
where we have dropped the subscripts on λ_{max} and ρ_{max} for simplicity, and ξ ≡ C/k, δ ≡ Y_{H}kP_{H}/C, and \(\beta \equiv Y_{\mathrm{H}}k\left( {\frac{{\lambda _{\mathrm{max}}}}{{Y_{\mathrm{F}}}} + P_{\mathrm{F}}} \right)/C\). The above equations represent the system of equations presented in the main text.
Analytical solution to the NSM
Equation (1) has three fixed points: two trivial fixed points at (F^{*}, H^{*}, R^{*}) = (0, 0, 0) and (0, 0, 1), and one nontrivial, internal fixed point at
where A = (λξρ + μσ) and B = (βμξ + δλξ − λμ). The stability of this fixed point is determined by the Jacobian matrix J, with \(J_{{{i}}j} = \partial \dot X_i/\partial X_j\), when evaluated at the internal fixed point, and X is the vector (F, H, R). The parameters in Eq. 1 are such that the real part of the largest eigenvalue of J is negative, so that the system is stable with respect to small perturbations from the fixed point. Because this fixed point is unique, it is the global attractor for all population trajectories for any initial condition where both the resource and consumer densities are nonzero.
Metabolic scaling relationships
The scaling relation between an organism’s metabolic rate B and its body mass M at reproductive maturity is known to scale as B = B_{0}M^{η}, where the scaling exponent η is typically close to 2/3 or 3/4 for metazoans^{47,56}, and has taxonomic shifts for unicellular species between η ≈ 1 in eukaryotes and η ≈ 1.76 in bacteria^{3,68}.
Several efforts have shown how a partitioning of B between growth and maintenance purposes can be used to derive a general equation for both the growth trajectories and growth rates of organisms ranging from bacteria to metazoans^{3,63,64,65,69,70}. This relation is derived from the simple balance condition \(B_{\mathrm{0}}m^\eta = E_{\mathrm{m}}\dot m + B_{\mathrm{m}}m{\kern 1pt} ,\)^{3,63,64,65,69,70} where E_{m} is the energy needed to synthesize a unit of mass, B_{m} is the metabolic rate to support an existing unit of mass, and m is the mass of the organism at any point in its development. This balance has the general solution^{3,64,71}
where, for η < 1, M = (B_{0}/B_{m})^{1/(1−η)} is the asymptotic mass, a = B_{0}/E_{m}, and m_{0} is mass at birth itself varying allometrically. We now use this solution to define the timescale for reproduction and recovery from starvation (Fig. 2; see ref. ^{64} for a detailed presentation of these timescales). The time that an organism takes to reach a particular mass εM is given by the timescale
where we define values of ε below to describe a variety of timescales, along with the rates related to τ. For example, the rate of reproduction is given by the timescale to go from the birth mass to the adult mass. The time to reproduce is given by Eq. 7 as t_{ λ } = τ(ε_{ λ }), where ε_{ λ } is the fraction of the asymptotic mass where an organism is reproductively mature and should be close to one (typically ε_{ λ } ≈ 0.95^{63}). Our reproductive rate, λ, is a specific rate, or the number of offspring produced per time per individual, defined as \(\dot F = \lambda F\). In isolation, this functional form gives the population growth \(F\left( t \right) = F_{\mathrm{0}}e^{\lambda t}\) that can be related to the reproductive timescale by assuming that when t = t_{ λ }, it is also the case that F = νF_{0}, where ν is the number of offspring produced per reproductive cycle. Following this relationship, the growth rate is given by λ = ln(ν)/t_{ λ }, which is the standard relationship^{70} and will scale as λ ∝ M^{η−1} for M >> m_{0} and any constant value of ε_{ λ }^{3,63,64,65,69}.
The rate of recovery ρ = 1/t_{ ρ } requires that an organism accrues sufficient tissue to transition from the hungry to the full state. Since only certain tissues can be digested for energy (e.g., the brain should not be degraded to fuel metabolism), we define the rates for starvation, death, and recovery by the timescales required to reach, or return from, specific fractions of the repletestate mass (Table 1). We define m_{ σ } = ε_{ σ }M, where ε_{ σ } < 1 is the fraction of repletestate mass where reproduction ceases. This fraction will deviate from a constant if tissue composition systematically scales with adult mass. For example, making use of the observation that body fat in mammals scales with overall body size according to M_{fat} = f_{0}M^{γ} and assuming that once this mass is fully digested and the organism starves, this would imply that ε_{ σ } = 1 − f_{0}M^{γ}/M. It follows that the recovery timescale, t_{ ρ }, is the time to go from mass m = ε_{ σ }ε_{ λ }M to m = ε_{ λ }M (Fig. 2). Using Eqs. 6 and 7, this timescale is given by simply considering the growth curve starting from a mass of \(m_{\mathrm{0}}' = \varepsilon _{\mathrm{\sigma }}\varepsilon _{\mathrm{\lambda }}M\), in which case
where \(a' = B_{\mathrm{0}}/E_{\mathrm{m}}'\) accounts for possible deviations in the biosynthetic energetics during recovery. It should be noted that more complicated ontogenetic models explicitly handle storage, whereas this feature is implicitly covered by the body fat scaling in our framework.
To determine the starvation rate, σ, we are interested in the time required for an organism to go from a mature adult that reproduces at rate λ, to a reducedmass hungry state where reproduction is impossible. For starving individuals, we assume that an organism must meet its maintenance requirements by using the digestion of existing mass as the sole energy source. This assumption implies the metabolic balance \(\dot mE_{\mathrm{m}}' =  B_{\mathrm{m}}m\) or \(\dot m =  a'm/M^{1  \eta }\), where \(E_{\mathrm{m}}'\) is the amount of energy stored in a unit of existing body mass, which differs from E_{m}, the energy required to synthesize a unit of biomass. Given the replete mass, M, of an organism, the above energy balance prescribes the mass trajectory of a nonconsuming organism: \(m\left( t \right) = Me^{  a't/M^{1  \eta }}\). The timescale for starvation is given by the time it takes m(t) to reach ε_{ σ }M, which gives
The starvation rate is then σ = 1/t_{ σ }, which scales with repletestate mass as \(M^{\eta  1}{\rm{ln}}\left( {1  f_{\mathrm{0}}M^\gamma /M} \right)^{1}\). An important feature is that σ does not have a simple scaling dependence on λ, which is important for the dynamics that we later discuss.
The time to death should follow a similar relation, but defined by a lower fraction of repletestate mass, m_{ μ } = ε_{ μ }M where ε_{ μ } < ε_{ σ }. Suppose, for example, that an organism dies once it has digested all fat and muscle tissues, and that muscle tissue scales with body mass according to M_{musc} = u_{0}M^{ζ}. This gives \(\varepsilon _{\mathrm{\mu }} = 1  \left( {f_{\mathrm{0}}M^\gamma + u_{\mathrm{0}}M^\zeta } \right)/M\). Muscle mass has been shown to be roughly proportional to body mass^{72} in mammals and thus ε_{ μ } is merely ε_{ σ } minus a constant. The time to go from starvation to death is the total time to reach ε_{ μ }M minus the time to starve, or \(t_{\mathrm{\mu }} =  M^{1  \eta }{\rm{ln}}\left( {\varepsilon _{\mathrm{\mu }}} \right)/a'  t_{\mathrm{\sigma }}\), and μ = 1/t_{ μ }.
Parameter values and estimates
All of the parameter values employed in our model have either been directly measured in previous studies or can be estimated from combining several previous studies. Below, we outline previous measurements and simple estimates of the parameters.
Metabolic rate has been generally reported to follow an exponent close to η = 0.75^{63,64,65}. We make this assumption in the current paper, although alternate exponents, which are known to vary between roughly 0.25 and 1.5 for single species^{64}, could be easily incorporated into our framework. The exponent not only defines several scalings in our framework, but also the value of the metabolic normalization constant, B_{0}, given a set of data. For mammals, the metabolic normalization constant has been reported to vary between 0.018 W g^{−0.75} and 0.047 (W g^{−0.75}; refs. ^{63,65}, where the former value represents basal metabolic rate and the latter represents the field metabolic rate). We employ the field metabolic rate for our NSM model that is appropriate for active mammals (Table 1).
An important feature of our framework is the starting size, m_{0}, of a mammal that adjusts the overall timescales for reproduction. This starting size is known to follow an allometric relationship with adult mass of the form m_{0} = n_{0}M^{υ} where estimates for the exponent range between 0.71 and 0.94 (see ref. ^{73} for a review). We use m_{0} = 0.097M^{0.92} ^{74} that encompasses the widest range of body sizes^{73}.
The energy to synthesize a unit of biomass, E_{m}, has been reported to vary between 1800 and 9500 (J g^{−1})^{63,64,65} in mammals with a mean value across many taxonomic groups of 5774 (J g^{−1})^{64}. The unit energy available during starvation, E′, could range between 7000 (J g^{−1}), the return of the total energy stored during ontogeny to a biochemical upper bound of E′ = 36,000 (J g^{−1}) for the energetics of palmitate^{65,75}. For our calculations, we use the measured value for bulk tissues of 7000 which assumes that the energy stored during ontogeny is returned during starvation^{65}.
For the scaling of body composition, it has been shown that fat mass follows M_{fat} = f_{0}M^{γ}, with measured relationships following 0.018M^{1.25} ^{76}, 0.02M^{1.19} ^{77}, and 0.026M^{1.14} ^{78}. We use the values from^{77} that falls in the middle of this range. Similarly, the muscle mass follows M_{musc} = u_{0}M^{ζ} with u_{0} = 0.383 and ζ = 1.00^{78}.
Typically, the value of ξ = C/k should roughly be 2. The values of ρ, λ, σ, and μ are all simple rates (note that we have not rescaled time in our nondimensionalization) as defined in the main text. Given that our model considers transitions over entire stages of ontogeny or nutritional states, the value of Y must represent yields integrated over entire life stages. Given an energy density of E_{d} = 18,200 (J g^{−1}) for grass,^{79} the maintenance value is given by P_{F} = B_{0}M^{3/4}/ME_{d}, and the yield for a full organism will be given by Y_{F} = ME_{d}/B_{ λ } (g individual g grass ^{−1}), where B_{ λ } is the lifetime energy use for reaching maturity given by
Similarly, the maintenance resource consumption rate for hungry individuals is P_{H} = B_{0}(ε_{ σ }M)^{3/4}/(ε_{ σ }M)E_{d}, and the yield for hungry individuals (representing the cost on resources to return to the full state) is given by Y_{H} = ME_{d}/B_{ ρ } where
Taken together, these relationships allow us to calculate ρ, δ, and β.
Finally, the value of α can be roughly estimated by the NPP divided by the corresponding biomass densities. From the data in Ref. ^{80}, we estimate the value of α to range between 2.81 × 10^{−10} (s^{−1}) and 2.19 × 10^{−8} (s^{−1}) globally. It should be noted that the value of α sets the overall scale of the F^{*} and H^{*} steady states along with B_{tot} for each type. As such, we use α as our fit parameter to match these steady states with the data from Damuth^{25}. We find that the best fit is α = 9.45 × 10^{−9} (s^{−1}) that compares well with the calculated range above. However, two points are important to note here: first, our framework predicts the overall scaling of F^{*} and H^{*} independently of α and this correctly matches data, and second, both the asymptotic behavior and slope of F^{*} and H^{*} are independent of α, such that our prediction of the maximum mammal size does not depend on α.
Rate equations for competitors with modified body mass
A resident population with mass M competes for resources with a closely related species with an altered mass M′ = M(1 + χ) where χ varies between χ_{min} < 0 and χ_{max} > 0, where χ < 0 denotes a leaner competitor and χ > 0 denotes a competitor with additional reserves of body fat. Importantly, we assume that the competing and resident individuals have the same quantity of nonfat tissues. For the allowable values of χ, the adjusted mass should exceed the amount of body fat, 1 + χ > ε_{ σ }, and the adjusted time to reproduce must be positive, which given our solution for τ(ε) (Eq. 7), implies that \(1  \varepsilon _{\mathrm{\lambda }}^{1  \eta }\left( {1 + \chi } \right)^{1  \eta } > 0\). Together, these conditions imply that χ ∈ (−f_{0}M^{γ−1},1/ε_{ λ }− 1) where the upper bound approximately equals 0.05.
Although the starved state of competing organisms remains unchanged, the rate of starvation from the modified full state to the starved state, the rate of recovery from the starved state to the modified full state, and the maintenance rates of both will be different, such that σ′ = σ(M′), ρ′ = ρ(M′), β′ = β(M′), and δ′ = δ(M′). Rates of starvation and recovery for the competing population are derived by adjusting the starting or ending state before and after starvation and recovery, leading to the following timescales:
The maintenance rates for the competing population require more careful consideration. First, we must recalculate the yield Y, as it must now be integrated over life stages that have also been slightly modified by the addition or subtraction of body fat reserves. Given an energy density of E_{d} = 18,200 (J g^{−1}) for grass^{80}, the maintenance value of the invading population is given by P_{F} = B_{0}(1 + χ)M^{3/4}/(1 + χ)ME_{d}, and the yield for a full organism will be given by \(Y_{\mathrm{F}} = (1 + \chi )ME_{\mathrm{d}}/B_{\mathrm{\lambda }}'\) (g individual g grass ^{−1}) where \(B_{\mathrm{\lambda }}'\) is the lifetime energy use for the competing population reaching maturity given by
where
Note that we do not use this timescale to determine the reproductive rate of the competitor—which is assumed to remain the same as the resident population—but only to calculate the lifetime energy use. Similarly, the maintenance for hungry individuals \(P_{\mathrm{H}}' = B_{\mathrm{0}}(\varepsilon _{\mathrm{\sigma }}(1 + \chi )M)^{3/4}/(\varepsilon _{\mathrm{\sigma }}(1 + \chi )M)E_{\mathrm{d}}\) and the yield for hungry individuals (representing the cost on resources to return to the full state) is given by \(Y_{{\mathrm H}'} = (1 + \chi )ME_{\mathrm{d}}/B_{{\mathrm \rho }'}\) where
Finally, we can calculate the maintenance of the competitors as
To determine whether or not the competitor or resident population has an advantage, we compute R*(M) and R*(M′ = M(1 + χ)) for values of χ ∈ (−f_{0}M^{γ−1},1/ε_{ λ }− 1), and the competing population is assumed to have an advantage over the resident population if R*(M′) < R*(M).
Data availability
Previously published data from Damuth (available in ref. ^{25}) were used for comparison with the model, and published parameter values are given in Table 1.
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Acknowledgements
We thank Luis Bettencourt, Jean Philippe Gibert, Eric Libby, and Seth Newsome for helpful discussions and comments on the manuscript. J.D.Y. was supported by startup funds at the University of California, Merced, and an Omidyar Postdoctoral Fellowship at the Santa Fe Institute. C.P.K. was supported by an Omidyar Postdoctoral Fellowship at the Santa Fe Institute. S.R. was supported by grants DMR1608211 and 1623243 from the National Science Foundation, and by the John Templeton Foundation, all at the Santa Fe Institute. The opinions expressed in this paper are those of the authors and do not necessarily reflect those of the funders.
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Yeakel, J.D., Kempes, C.P. & Redner, S. Dynamics of starvation and recovery predict extinction risk and both Damuth’s law and Cope’s rule. Nat Commun 9, 657 (2018). https://doi.org/10.1038/s4146701802822y
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DOI: https://doi.org/10.1038/s4146701802822y
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