CHIN. PHYS. LETT. Vol. 27, No. 1 (2010) 018701 Competitive Exclusion Principle Revised by Noise * LIU Yong-Jiang(刘永姜)** , WAN GAi-Ling(王爱玲), WANG Biao(王彪), LIU Zhao-Hua(刘兆华) Key Laboratory for AMT Shanxi, North University of China, Taiyuan 030051 (Received 7 September 2009) A fundamental tenet in theoretical ecology is the competitive exclusion principle. Two competitive species for a limited resource cannot coexist and thus one of the species will be driven to extinction. However, we show that noise can revise this principle in a resonance-like manner, which makes coherence resonance in the system. Our obtained results well enrich the findings in the interaction of populations in ecosystems, which may explain some filed observations in the real world. PACS: 87. 23. Cc, 82. 40. Ck, 05. 45. Pq DOI: 10.1088/0256-307X/27/1/018701 Competitive exclusion principle is one of most fundamental rules in ecosystems. More specifically, two species competing for a resource cannot coexist and one of the species may disappear. This principle is supported by many mathematical models, in which the Lotka–Volterra model for two competing species is the most famous. On the other hand, laboratory experiments play an important role in supporting the competitive exclusion principle in ecosystems. One series of laboratory studies was conducted by Park and Mertz using two species of flour beetles (of the genus Tribolium).[1−5] Park and his collaborators used a difference equation model in these studies, rather than the Lotka–Volterra differential equations.[6] They did not give a mathematical analysis of their model in detail, but they worked under the assumption that the model possesses the same dynamic scenarios as the Lotka–Volterra model. However, noise has long been considered an important factor that should be included in the modeling of ecological systems. Holling emphasized the importance of environmental variability in ecological dynamics and resilience.[7] Inherent uncertainties in an ecological system (e.g. varying rainfall or the nutrient inputs) widely exist. Additionally, there are considerable anthropogenic disturbances that exacerbate the uncertainty in the way an ecosystem responds.[8] Besides random fluctuations, there are also seasonal variations in different ecological parameters.[9,10] Some people consider the effects of seasonality on the phytoplankton enrichment in lakes.[9] And some groups have investigated the effect of noise in ecologically relevant models. The influence of noise in the input levels to a lake, determined by maximizing benefits or utility on optimal policy choices, has been well investigated.[10] Thus, when studying the interactions of different populations, noise can not be ignored. We firstly consider a classical Lotka–Volterra model of two-species competition[11,12] defined by the equations 𝑑𝑢 = 𝑟𝑢(1 − 𝑢 − 𝛼𝑣), (1a) 𝑑𝑡 𝑑𝑣 = 𝑟𝑣(1 − 𝛼𝑢 − 𝑣), (1b) 𝑑𝑡 where 𝑢 and 𝑣 are the population densities, 𝑟 is the growth rate of 𝑢 and 𝑣, and 𝛼 accounts for the interactions among the species. This Lotka–Volterra model has been widely studied, and it is well known that, for 𝛼 < 1, both species are present, but for 𝛼 > 1, exclusion takes place through a symmetry-breaking bifurcation and one of the species is eliminated.[12] Combining with noise term, we have the system as follows: 𝑑𝑢 = 𝑟𝑢(1 − 𝑢 − 𝛼𝑣), (2a) 𝑑𝑡 𝑑𝑣 = 𝑟𝑣(1 − 𝛼𝑢 − 𝑣) + 𝜂(𝑟, 𝑡). (2b) 𝑑𝑡 In Eq. (2), the stochastic factors are taken into account as the term, 𝜂(𝑟, 𝑡), which is obtained from microscopic interaction in the space[13−15] where the typical white noise will emerge. Recently, colored noise and white noise have both been used in describing ecological evolution.[16−18] White noise is the limiting case of colored noise, so we consider the more general case-colored noise. Due to the coupling, the noise in Eq. (2b) will have an influence on Eq. (2a) as well. Hence, we only need consider the noise presented in one of Eqs. (2a) and (2b) (here, we consider noise presented in Eq. (2b)). The noise term 𝜂(𝑟, 𝑡) is introduced additively in space and time, which is the Ornstein–Uhlenbech process that obeys the stochastic partial differential equation[19,20] 1 1 𝜕𝜂(𝑟, 𝑡) = − 𝜂(𝑟, 𝑡) + 𝜉(𝑟, 𝑡), 𝜕𝑡 𝜏 𝜏 (3) where 𝜉(𝑟, 𝑡) is a Gaussian white noise with zero mean and correlation, ⟨𝜉(𝑟, 𝑡)⟩ = 0, (4a) * Supported by the PhD Research Fund of the Ministry of Education of China under Grant No 20050204JJ, and the Natural Science Fund of the Shanxi Province (20040202JJ). ** Email: [email protected] c 2010 Chinese Physical Society and IOP Publishing Ltd ○ 018701-1 CHIN. PHYS. LETT. Vol. 27, No. 1 (2010) 018701 The colored noise 𝜂(𝑟, 𝑡), which is temporally correlated and white in space, satisfies ⟨𝜂(𝑟, 𝑡)𝜂(𝑟′ , 𝑡′ )⟩ = (︁ |𝑡 − 𝑡′ | )︁ 𝜀 𝛿(𝑟 − 𝑟′ ), exp − 𝜏 𝜏 (5) where 𝜏 controls the temporal correlation, and 𝜀 measures the noise intensity. We will systematically analyze effects of nonzero 𝜎 and 𝜏 on the competitive model for 𝛼 > 1, with the aim of reporting noise-induced transitions in a resonance-like manner depending on 𝜎 and 𝜏 , thus evidencing coherence resonance in the studied system and revising the competitive exclusion principle. The Runge–Kutta method is used for the deterministic part in Eq. (2). The stochastic partial differential Eq. (3) is integrated numerically by applying the Euler method. Several different discrete methods (simple Euler and Runge–Kutta) have been checked, and the results are almost the same. The code is implemented in Matlab 7.3 and the 𝑤𝑔𝑛 function is used for the main numerical integration. In Figs. 1 and 2, we show the time series of the two populations without noise. One can see from that the population 𝑢 always tends to extinction and 𝑣 persist. That is to say, if the initial value of the population is smaller, it will disappear regardless of the parameter values, which is called the competitive exclusion principle. 1.0 by nonzero values of 𝜎 in a resonant manner. More specifically, small 𝜎 are able to sustain only small density of 𝑢. As 𝜎 increases, the density of 𝑢 will reach the maximal value at a certain value of 𝜎. For the larger 𝜎, the intensity of 𝑢 is small. In other words, results presented in Fig. 3 thus indicate a typical coherence resonance scenario.[21−24] 1.0 (a) 0.8 u (4b) 0.6 0.4 0.2 0.0 1.0 (b) 0.8 v ⟨𝜉(𝑟, 𝑡)𝜉(𝑟′ , 𝑡′ )⟩ = 2𝜀𝛿(𝑟 − 𝑟′ )𝛿(𝑡 − 𝑡′ ). 0.6 0.4 0.2 0 5 10 15 Time t 20 25 30 Fig. 2. Time series of two populations. Parameter values are taken as 𝑟 = 0.5 and 𝛼 = 5, and the initial conditions are 𝑢(0) = 0.9 and 𝑣(0) = 1. 0.8 (a) 0.6 0.8 0.4 u u 0.6 0.4 0.2 0.2 0 10 0 0 (b) 0.4 0.6 0.8 Fig. 3. An illustration of intensity of 𝑢 for different values of noise intensity. Note that, for the no-noise model, the intensity of population 𝑢 will tends to zero. Coherence resonance occurs when combined with noise. Here 𝑟 = 0.5, 𝛼 = 1, 𝜏 = 6, and the initial conditions are 𝑢(0) = 1 and 𝑣(0) = 10. v 6 4 2 0 0 0.2 Noise intensity σ 8 5 10 Time t 15 20 Fig. 1. Time series of two populations. Parameter values are taken as 𝑟 = 0.5 and 𝛼 = 1, and the initial conditions are 𝑢(0) = 1 and 𝑣(0) = 10. Now, we consider the effect of noise on the intensity of 𝑢. We run the simulations until the intensity of 𝑢 reaches a fixed values or until it shows a behavior that does not seem to change its characteristics any longer. The results presented in the panels of Fig. 3 clearly show that the density of 𝑢 will larger than zero The role of temporal correlation 𝜏 of the colored noise is also significant including its intensity in controlling the intensity of the population 𝑢. Now, it is natural to ask what the consequence of the temporal correlation of the colored noise is. In order to well understand that mechanism, we also perform a series of simulations for fixed noise intensity 𝜀, which is shown in Fig. 4. We choose a set of 25 parameters for numerical simulations. We find that, when 𝜏 < 3.5 or 𝜏 > 10, noise has no effect on the intensity of 𝑢. How- 018701-2 CHIN. PHYS. LETT. Vol. 27, No. 1 (2010) 018701 ever, when 𝜏 ∈ (3.5, 10), the intensity of 𝑢 is more than zero, which is induced by noise, and reaches the maximum value at 𝜏 ≈ 6. meaningful suggestions given. References 0.46 [5] 0.23 [6] [7] [8] u 0.69 [1] [2] [3] [4] 0 0 4 8 12 Temporal correlation t [9] [10] [11] 16 Fig. 4. An illustration of intensity of 𝑢 for different values of temporal correlation. Here 𝑟 = 0.5, 𝛼 = 1, 𝜎 = 0.3, and the initial conditions are 𝑢(0) = 1 and 𝑣(0) = 10. In summary, we have shown that color noise introduced in the system of a competitive model can revise the competitive exclusion principle in a resonant manner depending on the intensity of noise and temporal correlation. The reported phenomenon is identical as coherence resonance reported previously in temporal and spatially extended dynamical systems.[21,22] Ecologically speaking, noise effect should not be neglected when considering the interaction of the populations, which may have an effect on the dynamics behavior, particularly in revising some rules in the ecosystem.[25,26] We are grateful to the anonymous referees for the [12] [13] [14] [15] [16] [17] [18] [19] [20] [21] [22] [23] [24] [25] [26] 018701-3 Park T 1948 Ecol. Monogr. 18 265 Park T 1954 Physiol. Zool. 27 177 Park T 1957 Physiol. 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