The dynamics of an age structured predator–prey model with disturbing pulse and time delays☆
Introduction
Effectively controlling pests has become an increasingly complex issue over the past two decades. A wide range of pest control ways are available to farmers such as biological, cultural, physical and chemical tools. Farmers often use relatively simple techniques to control the increase in insect pest amounts regardless of the balance of nature. For example, farmers often catch pests by mechanical tools or poison pests by the overuse of pesticides. However, on the one hand, overuse of chemicals have created many ecological and sociological problems, hence chemical control now needs to be used reasonably. On the other hand, eradication for pests is difficult both practically and economically as pests can breed quickly. Therefore, it may be the best way of ensuring that pest populations do not fluctuate widely from one year to the next.
Most pests have their natural enemies, and these natural enemies can effectively suppress pests sometimes. When people catch or poison pests, pests and their natural enemies, which does die out earlier? For example, field mouses and owls lived in the northwest plain of China in 1998. The owls (natural enemy) became extinct earlier than field mouses, because the prey (pest) is catched or poisoned largely, subsequently, the survivor (field mouse) increased rapidly and overran ultimately, why? We would like to answer the question, then we need to investigate the effect of the harvesting for pests on its natural enemies. In practice, from the principle of ecosystem balance, we need only to control the pest population under the economic threshold level (ETL) and not to eradicate natural enemy totally, and hope pest population and natural enemy population can coexist when the pests do not bring about immense economic losses. In this paper, according to the above ecological background, we consider the prey-dependent consumption predator–prey (natural enemy–pest) models with age structure for the predator, the prey is catched or poisoned impulsively, details can be seen in Sections 2 and 5. In Section 3, We prove that, when the impulsive period is no longer than some threshold, i.e. or partial destruction to pests (preys) by catching or pesticides is at a appropriate extent, i.e. , the predator-eradication periodic solution is globally attractive, or say, the predator population can be eradicated totally when the pest population is catched or poisoned at a certain extent. However, from the point of ecological balance and saving resources, we only need to control the pest population under the ETL in order not to eradicate predator (natural enemy) totally, so in Section 4, we further prove that, when the impulsive period is longer than the threshold, i.e., or partial destruction to pests (preys) by catching or pesticides is smaller than the threshold, i.e., , pest population and natural enemy population can coexist and the system is uniformly permanent.
The predator–prey models with age structure for the predator were introduced or investigated by Hastings, Wang and Hui [4], [5], [6], [7], [21]. Since the immature predator takes (which is called maturation time delay) units of time to mature, the death toll during the juvenile period should be considered, so, time delays have important biological meanings in age-structured models. Hence many age-structured models with time delay were extensively studied (see [6], [21], [4], [13], [14], [18], [16], [22], [1]). In recent years, impulsive systems are found in many domains of applied sciences (see [7], [19], [3], [11], [17], [20], [12], [24]). The investigation of impulsive delay differential equations is inchoate, and impulsive delay differential equations are almost analyzed in theory (see [23], [10], [15]). Time delay and impulse are introduced into predator–prey models with stage structure, which greatly enriches biologic background, but the system become nonautonomous and quite complicated, which causes us greatly difficulties to study the model. Therefore, the literature on global qualitative analysis for delay stage-structured models with impulse effect has never been seen by now. In present paper, we propose a new delay predator–prey model with age structure and impulsive effect and method which is applied to study impulsive delay differential equations.
Section snippets
Model and preliminaries
The predator–prey model with age structure for the predator was introduced by Hastings [5], [6]:where represent the densities of prey, immature and mature predator, respectively, r is the logistic intrinsic growth rate of the prey in the absence of the predator, is the predation rate of predator and represents the conversion rate at which ingested prey in excess of what is needed for maintenance is translated into predator
Existence of a ‘predator-extinction’ periodic solution
We begin the analysis of (2) by first demonstrating the existence of a ‘predator-extinction’ solution, in which predator individuals are entirely absent from the population permanently, i.e.,This is motivated by the fact that is an equilibrium solution for the variable , as it leaves . Under these conditions, we show below that the prey population oscillates with period T in synchronization with the periodic impulsive catching or pesticides.
Assuming (4), we know
Uniform permanence
In Section 3, we have proved that, when or , the ‘predator-extinction’ periodic solution is globally attractive, that is, when the pest population is catched or poisoned largely, the natural enemy population is eradicated totally. In practice, from the principle of ecosystem balance and in order to save resources, we only need to control the pest population under the ETL, and not to
Numerical analysis and discussion
In this paper, we introduce a time delay and pulse into the prey-dependent consumption predator–prey (natural enemy–pest) models with age structure for the predator, and theoretically analyze the influence of impulsive catching or poisoning for the prey and juvenile period of the predator on predator-extinction and the permanence of the populations. To facilitate the interpretation of our mathematical findings and possible lab or field implementation of the model and to investigate the effect
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This work is supported by National Natural Science Foundation of China (10471117) and Natural Science Foundation of SDUST (05g016).