Department of Civil and Environmental Engineering, MIT, 77 Massachusetts Av., Cambridge, MA 02139, USA.
Department of Biology - Ecology and Evolution, University of Fribourg Chemin du Musée 10, Fribourg CH-1700, Switzerland.
J Theor Biol. 2018 Aug 7;450:30-36. doi: 10.1016/j.jtbi.2018.04.030. Epub 2018 Apr 24.
The feasibility domain of an ecological community can be described by the set of environmental abiotic and biotic conditions under which all co-occurring and interacting species in a given site and time can have positive abundances. Mathematically, the feasibility domain corresponds to the parameter space compatible with positive (feasible) solutions at equilibrium for all the state variables in a system under a given model of population dynamics. Under specific dynamics, the existence of a feasible equilibrium is a necessary condition for species persistence regardless of whether the feasible equilibrium is dynamically stable or not. Thus, the size of the feasibility domain can also be used as an indicator of the tolerance of a community to random environmental variations. This has motivated a rich research agenda to estimate the feasibility domain of ecological communities. However, these methodologies typically assume that species interactions are static, or that input and output energy flows on each trophic level are unconstrained. Yet, this is different to how communities behave in nature. Here, we present a step-by-step quantitative guideline providing illustrative examples, computational code, and mathematical proofs to study systematically the feasibility domain of ecological communities under changes of interspecific interactions and subject to different constraints on the trophic energy flows. This guideline covers multi-trophic communities that can be formed by any type of interspecific interactions. Importantly, we show that the relative size of the feasibility domain can significantly change as a function of the biological information taken into consideration. We believe that the availability of these methods can allow us to increase our understanding about the limits at which ecological communities may no longer tolerate further environmental perturbations, and can facilitate a stronger integration of theoretical and empirical research.
生态群落的可行性域可以通过环境生物和非生物条件的集合来描述,在给定的地点和时间内,所有共存和相互作用的物种都可以在这些条件下拥有正丰度。从数学上讲,可行性域对应于在给定的种群动态模型下,系统中所有状态变量在平衡时具有正(可行)解的参数空间。在特定的动力学下,可行平衡点的存在是物种持续存在的必要条件,无论可行平衡点是否动态稳定。因此,可行性域的大小也可以用作群落对随机环境变化的容忍度的指标。这激发了丰富的研究议程来估计生态群落的可行性域。然而,这些方法通常假设物种相互作用是静态的,或者每个营养级的输入和输出能量流不受限制。然而,这与自然界中群落的行为方式不同。在这里,我们提出了一个逐步的定量指南,提供了说明性的例子、计算代码和数学证明,以系统地研究在种间相互作用变化下以及在不同的营养能流约束下生态群落的可行性域。该指南涵盖了可以由任何类型的种间相互作用形成的多营养级群落。重要的是,我们表明,可行性域的相对大小可以随着所考虑的生物信息的变化而显著变化。我们相信,这些方法的可用性可以帮助我们更好地理解生态群落可能不再容忍进一步环境干扰的极限,并促进理论和经验研究的更紧密结合。