Education empowers humans and gets them ready to face challenges of life efficiently. Literacy and social media campaigns make people aware of the tools and techniques requisite for protection against the emerging diseases. In this paper, we investigate the combined impacts of literacy and social media on the dynamics of infectious diseases spreading through direct contact. Normalized forward sensitivity indices explore the impacts of parameters on basic reproduction number. We perform global sensitivity analysis for the infective population with respect to some controllable epidemiologically important parameters. If the growth rate of broadcasting informations through social media is very high, the system shows limit cycle oscillations. On the other hand, the baseline number of social media advertisements stabilize the system by evacuating persistent oscillations and ultimately settling the system from stable endemic equilibrium to stable disease-free state. The dissemination of awareness among literate people also suppresses the prevalence of limit cycle oscillations and drives the system to disease-free zone. An extension in model is made by assuming the growth rate of social media advertisements as periodic function of time. The simulation results show that the nonautonomous system showcases periodic as well as higher periodic solutions on the increase in the growth rate of advertisements. Our results evoke that media and education play a tremendous role in mounting awareness among the population leading to elimination of disease in the society.
Citation: Rajanish Kumar Rai, Pankaj Kumar Tiwari, Yun Kang, Arvind Kumar Misra. Modeling the effect of literacy and social media advertisements on the dynamics of infectious diseases[J]. Mathematical Biosciences and Engineering, 2020, 17(5): 5812-5848. doi: 10.3934/mbe.2020311
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Abstract
Education empowers humans and gets them ready to face challenges of life efficiently. Literacy and social media campaigns make people aware of the tools and techniques requisite for protection against the emerging diseases. In this paper, we investigate the combined impacts of literacy and social media on the dynamics of infectious diseases spreading through direct contact. Normalized forward sensitivity indices explore the impacts of parameters on basic reproduction number. We perform global sensitivity analysis for the infective population with respect to some controllable epidemiologically important parameters. If the growth rate of broadcasting informations through social media is very high, the system shows limit cycle oscillations. On the other hand, the baseline number of social media advertisements stabilize the system by evacuating persistent oscillations and ultimately settling the system from stable endemic equilibrium to stable disease-free state. The dissemination of awareness among literate people also suppresses the prevalence of limit cycle oscillations and drives the system to disease-free zone. An extension in model is made by assuming the growth rate of social media advertisements as periodic function of time. The simulation results show that the nonautonomous system showcases periodic as well as higher periodic solutions on the increase in the growth rate of advertisements. Our results evoke that media and education play a tremendous role in mounting awareness among the population leading to elimination of disease in the society.
1.
Introduction
In the integrated pest management, chemical control is one of the main control tactics, and the pesticides and other chemicals for the pest management are employed in reality [1,2,3,4]. The emergence of chemical synthetic insecticides has made great contributions to the control of some vector insects, agricultural pests and infectious diseases spread by them. At the same time, chemical pesticides are easy to operate and can control pests quickly and effectively. Therefore, in a long time at present and in the future, it is still a favorable weapon to fight vector insects and agricultural pests in rural areas. However, due to the high frequency and large-scale use of pesticides all over the world, long term accumulation leads to the occurrence and development of resistance and serious environmental pollution, which results in the decrease of the sensitivity of pests to pesticides, so they are not inhibited or poisoned by pesticides[5,6,7,8].
Therefore, how to reduce or delay the resistance of pests to pesticides, how to make the pesticides play their role to the maximum extent, and how to reduce the impact of pesticides on the ecological environment are issues of agricultural administrative departments. The purpose of resistance management is to find appropriate ways to slow down and prevent the occurrence and development of pest resistance to pesticide, or restore resistant pest to a sensitive state. The key of resistance management is to reduce the selection pressure of pesticides on pests[9,10,11]. The development of pest resistance to pesticide is divided two types: external induced resistance and genetic resistance. The external induced resistance is that the pest developed the resistance to pesticide due to the large dosage and high frequency of pesticide spraying. Genetic resistance refers to the resistance generated by genetic inheritance of the resistance of the previous generation of pests to pesticides [12]. Since most of the pests that are sensitive to pesticides are killed during the use of pesticides, the surviving pests with pesticide resistance will pass on the resistance genes to the next generation. Therefore, with the change of generations, the proportion of pests carrying resistance genes becomes higher and higher, and the effect of pesticides gradually decreases, which seriously affects the success or failure of pest and disease control. In order to restrain the resistance of pest to pesticide, some principles have been proposed including rotation or switching between different types of pesticides, using biological control techniques, delaying the emergence of resistance, restoring the sensitivity of pests to pesticides and so on [13,14,15,16,17].
Recently, pest management models with pest resistance to pesticide have been widely studied. Dobson and May combining population dynamics and genetics modelled the development of pest resistance to pesticide [18]. Liang et al. developed a continuous pest population growth model with both evolution of pesticide resistance and instantaneous pesticide applications, and studied the optimal time for switching between different kinds of pesticides under three different threshold levels [10]. Considering the growth of most pest population is not continuous, the novel discrete pest population models with the evolution of pest resistance to pesticide have been proposed and analyzed by Liang et al, who studied the effects of complex dynamical behaviour of pest population on pesticide switching strategies[11]. The genetic resistance was ignored and they only considered the external induced resistance in all of those studies.
An interesting question is how to describe impulsive control strategies implemented within each generation when pests have non-overlapping generations, including impulsive release of natural enemies and spraying of pesticides. In order to solve this problem, some interesting modeling methods have been proposed recently. Tang et al. simplified hypothesis control strategy which is implemented at the beginning or the end of each generation [19]. Wang et al. first proposed a single population model with multiple impulsive pesticides applications within each generation, and then studied the existence and stability of the unique positive equilibrium[20]. Liang et al. proposed an analysis method of extended discrete model based on continuous logistic model under impulse perturbation to model the effects of single pesticide applications within each generation on populations growth[21].
Once the pest resistance to pesticide is genetic, the questions are how to model the external induced resistance and genetic resistance in pest control model, and how to management the pest resistance to pesticide to achieve the purpose of pest control to solve those problems, according to the genetic laws and pesticide spraying, we modeled a pest resistance to pesticide model combine the external induced resistance and genetic resistance. Then we introduce the pest resistance to pesticide model into pest control models, the threshold conditions of pest eradication were discussed. For resistance management, we discussed the pesticide switching strategy, and the optimal switching time was investigated under the control strategy of one times pest control within each pest generation and multiple pest control within each pest generation. Moreover, the effects of the death rate of susceptible pests, the spraying times of pesticide within each generation, the dominance of resistance allele on the pesticide switching generations were studied.
2.
The evolution of pesticide resistance and pest control model
As described in the first part of the introduction, the development of pests' resistance on pesticide has a significant impact on pest control. To address those effects, we first investigate the evolution of pests' resistance, i.e.. we will analyze the development of pests' resistance from the perspective of gene inheritance and establish the development equation of pests' resistance. Moreover, the evolution of pests' resistance has been combined into the pest growth model.
2.1. Simple genetic model with pesticide resistance
We assume that the pesticide resistance is determined by a single gene with two alleles R and S. R denotes the resistance allele which represents the ability to survive on pesticide spraying. S denotes the susceptibility allele which represents the ability to survive with no resistance to the pesticide. According to Mendelian genetic law, we divide the pest population into three different types: homozygote resistant individuals RR, homozygote susceptibles SS and heterozygotes RS. In the presence of an application of pesticide, we denote WRR, WRS, WSS are the fitness of RR type pest, the fitness of RS type pest and the fitness of SS type pest, respectively. Note that the fitness of an individual is independent of its genotype frequency [22], and we assume that pest individual is mated randomly. According to the hardy-weinberg principle [23], if the frequence of resistance allele is pn and the frequence of susceptible allele is qn in generation n (with pn+qn=1), then the genotype frequencies in pests after selection are given by the following equations
RRn=WRRp2n¯Wn,RSn=WRS2pnqn¯Wn,SSn=WSSq2n¯Wn,
where ¯Wn is the mean fitnesses with
¯Wn=p2nWRR+2pnqnWRS+q2nWSS.
The averages fitnesses of the resistance allele R at generation n is
wn=pnWRR+qnWRS.
Consequently, the frequence of the resistance allele R in generation n+1 becomes
pn+1=pnwn¯Wn=pn(pnWRR+qnWRS)¯Wn.
Submitting qn=1−pn, we have the evolution of pesticide resistance
2.2. The effects of frequency of pesticide spraying on evolution of resistance
From Eq (2.1), it is obvious to see that pn depends on the relative values of WRR, WRS and WSS. Now we focus on deriving equations that represent the fitness of the three different genotypes: RR, RS, and SS. We know that the death rate of pests strictly depends on the dosage of pesticide spraying. For simplification, we assume that the same dosage of pesticide is sprayed at each control event, and without loss of generality, we assume that one unit dose of pesticide is sprayed at each control event. Naturally, the homozygote susceptibles SS are assumed to die with a higher death rate d1(0≤d1≤1) when a single pest control is carried out with one unit dose of pesticide is sprayed (Note that the different pesticides have different d1, for convenience, we use d1 as death rate in the whole study. For the specific pesticide, we only need to give specific value of d1 in the following results). However, death rate is reduced by the level of dominance of pesticide resistance allele h(0≤h≤1) in RS individuals, thus, the death rate of heterozygous individuals is (1−h)d1 after one unit of sprayed pesticide. And the death rate of resistant individuals RR is d2, for simplicity, we assume that the death rate of resistant individuals RR extremely low, that is d2≈0. Consequently, the fitness of each genotype after pesticide is applied once within each generation is
WRR=W(1)RR=1,
WRS=W(1)RS=1−(1−h)d1,
WSS=W(1)SS=1−d1.
In reality, farmers usually spray pesticides multiple times within each pest generation. In order to investigate the evolution of pests' resistance in this case, we assume that the pesticide is sprayed M times (M≥1) within each generation, and the fitness of each genotype after m−times pesticide spraying in each generation is W(m)RR, W(m)RS, W(m)SS, (m=1,2,...M). We know that the fitness of homozygote sensitives WSS is W(1)SS=1−d1 for once pesticide spraying, W(2)SS=(1−d1)2 for 2−times pesticide spraying, ⋯, and the fitness of heterozygotes WRS is W(1)RS=1−(1−h)d1 for once pesticide spraying, W(2)RS=(1−(1−h)d1)2 for 2−times pesticide spraying⋯. Thus, the fitness of each genotype after spraying pesticide m times within each generation can be expressed as
W(m)RR=1,
W(m)RS=(1−(1−h)d1)m,
W(m)SS=(1−d1)m.
Thus, the frequence of genotypes after m times pesticide spraying in the nth generation are given by the following equations
If the pesticide have completely kill rate to the homozygote sensitives (i.e., d1=1 and W(M)SS=0), then
pn+1=pn(1−W(M)RS)+W(M)RSpn(1−2W(M)RS)+2W(M)RS.
(2.3)
Solving equation Eq (2.3) with initial gene frequency p0, we have
pn=β(p0−1)(W(M)RS)n−p0+β(p0−1)(W(M)RS)n−p0+β,
(2.4)
where β=W(M)RS2W(M)RS−W(M)RR.
In the next section, calculating the n is important to investigate the optimal generation for switching pesticide. From Eq (2.4), we can get
n=logW(M)RS(p0−β)(pn−1)(p0−1)(pn−β).
(2.5)
Now we consider the general case (i.e., W(M)SS≠0). In order to obtain pn or n, we calculate the amount of change in gene frequency per generation by using Haldance' method [29], i.e..
Case 3: R is incomplete dominant or incomplete recessive gene in RS, i.e., 0<h<1.
Integrating Eq (2.7) with the initial condition p0, we can get
n=[ln((pnp0)D(pn−1p0−1)E(GnG0)F)],
(2.10)
where D=W(M)SSW(M)RS−W(M)SS, E=−11−W(M)RS, F=W(M)RS2−W(M)SS(1−W(M)RS)(W(M)RS−W(M)SS) and Gn=(1−2W(M)RS+W(M)SS)pn+W(M)RS−W(M)SS. [a] denotes the greatest integer no larger than a.
Next, we investigate the effects of death rate of pesticide for homozygote susceptibles (d1) and the spraying times (M) on the frequence of resistance (pn). Because of the highly nonlinearity of Eq (2.10), we only focus on the effects in case 1 and case 2 theoretically, and for case 3, we just carry out some numerical simulations.
For case 1, i.e.. R is completely dominant gene in RS, differentiating Eq (2.8) with respect to d1 and M respectively, we have
From the above formulas, we can see that pn is an increasing function with respect to d1 and M in both case 1 and case 2. That is, decreasing the death rate of susceptible pests or decreasing the spraying times of pesticide in each generation can decrease the values pn. In order to show in more detail how the level of dominance of pesticide resistance allele h, the mortality rate d1 and M affect evolution of pesticide resistance, we analyze those by numerically simulation in Figure 1. From Figure 1 (a) and (c), we can see that the higher the efficiency of the pesticides (i.e. the higher mortality rate), the faster the resistance development is. From Figure 1 (b) and (d), we can see that the more times of the pesticide spraying in one generation, the faster the resistance development is.
Figure 1.
The effect of the mortality rate of susceptible pests d1 and spray times M on pn. (a)–(b) R is completely recessive gene in RS, (c)–(d) R is completely dominant gene in RS, (e)–(f) R is incomplete dominant or incomplete recessive gene in RS and p0=0.0001.
If we fix the frequence of resistance, then we want to know how the death rate (d1), spraying times (M) and the level of dominance of pesticide resistance (h) on generation (n) which reach to fixed resistance level. For this purpose, we carry out the sensitivity analysis of n in Figure 2. In Figure 2, we fix pn=50%, and we can see that the higher the efficiency of the pesticides is (i.e., the higher mortality rate), the faster of the pest population reaches the fixed resistance level; The more times of the pesticide sprayed in one generation, the faster of the pest population reaches the fixed resistance level; The higher the level of dominance of pesticide resistance, the faster of the pest population reaches the fixed resistance level.
Figure 2.
The effect of the mortality rate d1 and spraying times M on n, with the variation of h from 0 to 1 and p0=0.005.
Throughout this study, the pest population is assumed to grow logistically within each generation [n,n+1],
dx(t)dt=rx(t)(1−x(t)K),n≤t≤n+1,n=0,1,2,...,
(2.11)
where x(t) is the density of the pest population at time t, r denotes the intrinsic growth rate and K represents the carrying capacity.
In reality, people usually spray pesticide within a fairly short period, so it's reasonable to assume that the density of pests can be reduced instantaneously once the chemical control tactics are applied. Therefore, the impulsive hybrid model based on Eq (2.11) can be employed to depict this control measure.
If the pesticides is applied at time n+τm (0≤τm≤1) with an instantaneous killing rate Dn,m, then we have
It is clear that the instantaneous killing rate Dn,m decreases as pesticide resistance develops.
3.
Switching strategy for spraying once pesticide within each generation
In this section, we assume that once control is implemented within each pest generation. We then investigate how to switch pesticides and manage the development of genetic resistance such that the pest population can be eventually eliminated or maintained at a density below EIL. In order to investigate those questions, we propose two different switching strategies, and investigate the optimal switching times under once control within each generation.
3.1. Switching pesticide with threshold condition of pest eradication as a guide
We assume that pesticide was used once within each generation at time n+τ1 (0≤τ1≤1) in nth generation. The model Eq (2.12) becomes
Denote x(n)=xn, then we have the following iteration equation from nth generation to n+1th generation
xn+1=Ker(1−Dn)xnK+(erτ1Dn+er(1−Dn)−1)xn,
(3.3)
which is a non-autonomous Beverton-Holt difference equation, i.e. the so-called extended Beverton-Holt model. For more details of extended Beverton-Holt model, please see the references [32,33,34,35,36,37].
According to the properties of the extended Beverton-Holt model, we have that if er(1−Dn)<1, then the zero solution of Eq (3.3) is globally asymptotically stable. Consequently, we can define the threshold value Rn as
Rn=er(1−Dn),
(3.4)
where Dn can be calculated by Eq (2.13). Thus, the pest population will be eradicated if Rn<1 for all n=0,1,2,⋯.
Note that Rn is dynamic and depends on Dn. We can see that Dn is a monotonic decreasing function of n. Therefore, as the pest generations increases, the threshold value Rn increases and exceeds one, resulting in pest resurgence and outbreaks.
In Figure 3, we simulate the threshold Rn with different level of dominance of pesticide resistance allele in RS (h) and the mortality rate (d1), which reveal that Rn is an increasing function with respect to n, and will exceed 1 after several pesticide pesticide applications. From Figure 3 (a), we can see that the greater of h is, the faster growth of Rn is. This is because that the higher of the level of dominance of pesticide resistance allele in RS is, the faster development of the pests' resistance is. All those confirm that the pest population will be resurgence and outbreaks as the pesticide resistance evolution. From Figure 3 (b), it is obvious that the effects of mortality rates d1 on Rn are more complicated with the development of time n. The bigger d1 is, the smaller Rn is, when n is small. And with the increase of n, the effects of mortality rates d1 on Rn is changed, the bigger d1 is, the smaller Rn is. This is due to that in the early stages of the pest control, the more dosage of pesticide is sprayed, the higher of the mortality rate is, and the pest population is more easy to control with the high efficiency of pesticide. With the increasing of n, the pest control times is increasing, and the pest's resistance is developed, which the results is the decline in efficiency of pesticide, and the pests' outbreak.
Figure 3.
The effects of the level of dominance of pesticide resistance allele h and the mortality rate d1 on the Rn. The other parameters are given as follows: r=0.65, p0=0.0001; (a): d1=0.7; (b): h=0.65.
In order to prevent pest population outbreaks and restrain the development of pesticide resistance, farmers usually switch some different type pesticide. And what is the optimal switching time with the aim of eradication of pest population. For this aim, we only need the threshold Rn below one for all n=0,1,2,⋯. Therefore, farmers need to switch the pesticide before the threshold value Rn goes to one. Without loss of generality, we assume that the threshold value Rn will increase and exceed the unit after n1th generation i.e
n1=max{n:Rn≤1},
and the optimal switching time is n1, or the maximum number of one type of pesticide spraying is n1+1 (note that the first pesticide application is at time n=0). That is, after n1+1 times pesticide spraying, farmers should switching another type of pesticide.
In order to determine n1 analytically, we let Rn=1, then
The Eq (3.6) becomes to f(pn)=0. Now we solve this equation with respect to pn, and substituting pn=pn1 into Eq (2.5) or Eqs (3.10)–(2.10), we can obtain the optimal switching time n1 under different cases.
The detailed calculation of the pn1 is provided in Appendix A.
Now we turn our attention to the effect of the timing of pesticide applications τ1 on the density of pest population xn. From Eq (3.3) we have the following iteration equation
It's easy to see that xn is a decreasing function with respect to τ1, this means that the later of pest control is, the smaller of pest population density is, and more benefit to pest control. In Figure 4, we simulate the development of xn with respect to n under different τ1. From Figure 4, we can see that the later insecticide spraying time is, the smaller the population density is, and we also see that the density of pest population xn is decreasing at the beginning of pest control, and then the density of pest population xn is increasing after some pesticide applications. The reason is that with the increasing of number of pesticide sprayings, the pesticide resistance is developed, and consequently, the density of pest population can not decrease any more, instead, it increases rapidly, even exceeds the EIL.
Figure 4.
The effects of the time factor τ1 on the density of xn predicated by Eq (3.3) for τ1=0.1, τ1=0.5, τ1=0.9, respectively. The parameter values are fixed as follows: r=0.65, η=80, x0=20, d1=0.55, h=0.65, p(1)=0.0001, EIL=35.
As mentioned in the introduction, the pre-set goal of the pest management is to control the density of the pest below the EIL. However, the pest population will exceed the EIL eventually if only one type of pesticide is used (i.e. do not switch pesticides), see Figure 4. Thus, in order to successfully control the density of pest population below the EIL, farmers should switch another kind of pesticide before the density of pest population reach to EIL. In this subsection, we will investigate the optimal switching time with EIL as switching guide.
In there, we assume that the pest population density exceeds EIL for the first time in the n2+1th generation.This indicates that xn2≤EIL and xn2+1>EIL, that is the optimal switching generation is n2+1.
where E1=(er−1)(K−EIL)er(K−EIL)+EILerτ1. It is easy to see that E1 is decreasing as τ1→1. This implies that n2 is increasing as τ1→1, in other words, under the EIL guided switching strategy, the number of the same pesticide used increases with the increasing of τ1.
where Zn2=(K−EIL)Nn2+1−EIL∑n2i=1(er(i+τ1)Di∏i−1j=0(1−Dj)).
Therefore,
n2=[{l|Zl=EILK+x0EILD0erτ1−EILx0x0}].
(3.12)
In order to understand these two different switching strategies more intuitively, we draw some numerical simulations in the Figure 5. From Figure 5 (a) we can see that under the Rn guided switching strategy the pest population will be eradicated completely after several pesticide switches, where n1=3. That is after four pesticide applications of one kind of pesticide (note that the first pesticide application is at time n=0), the farmers must switch to another kind of pesticide to eradicate the pest quickly. From Figure 5 (b) we can see that under the EIL guided switching strategy pest control will tends to periodic control after a certain number of pesticide switches. This is due to the development of resistance of pest on the same type pesticide, the density of pest population will exceed EIL after some numbers of the same type pesticide spraying, under the EIL guided switching strategy pest control, farmers should switching another type of pesticide at the last number of pesticide spraying before the density of pest population reach to EIL (we assume that the pest population has the same development of pesticide resistance on different type of pesticide), due to the same process of pesticide resistant evolution and pest control period, the pest control will tends to periodic control under this switching strategy.
Figure 5.
Illustrations of two different switching strategies.The parameter values are fixed as follows:r=0.6, K=50, x0=20, τ1=0.9, d1=0.65, h=0.65, p0=0.005, EIL=35. (a) Numerical simulations of Eq (3.3) with several pesticides switches guided by threshold condition; (b) Numerical simulations of Eq (3.3) with several pesticides switches guided by the EIL.
4.
Multiple control actions applied within each generation
In reality, the pesticide is sprayed for multiple times in each generation to control pest. Therefore, in this section, we developed an extended discrete single population model with multiple impulsive chemical control within each generation, and then investigate the optimal generation for switching pesticides.
4.1. Switching pesticide with threshold condition as a guide
We assume that the pesticides are applied M times within each generation, that is to see, there exist τm(m=1,2⋯,M) with n≤n+τ1≤n+τ2≤⋯≤n+τM≤n+1, such that the pesticides have been applied at n+τm with a proportion Dn,m of the pest being killed. We have
For convenience, we denote Dn,0=0. Therefore, by employing the same methods proposed before, we have the following extended discrete single population model with multiple impulsive chemical control within each generation
In particular, if M=1 then we have ∑Mm=1(erτmDn,m∏mj=1(1−Dn,j−1))=erτ1Dn.
For simplicity, we assume that the pesticides are sprayed periodically within each generation, which satisfies τm+1−τm=T for m = 1, 2..., M and 0<T≤1−τ1M−1, thus we can get
xn+1=KλnxnK+(μn+λn−1)xn,
(4.3)
with λn=er∏Mm=1(1−Dn,m) and μn=∑Mm=1(er(τ1+(m−1)T)Dn,m∏mi=1(1−Dn,i−1)). Note that this is the extended Beverton-Holt model, and if er∏Mm=1(1−Dn,m)<1, the population size is gradually reduced and becomes extinct eventually. We can define the dynamic threshold value RMn as follows:
RMn=erM∏m=1(1−Dn,m),
that is, if RMn<1, the population size is gradually reduced and becomes extinct eventually.
In order to analyse the effects of the spraying times M of pesticides in each generation on the threshold value RMn, we simulate the threshold value RMn with different spraying times M in Figure 6. From Figure 6, we can see that RMn is a decreasing function with respect to M, that is, the more spraying times in each generation is, the later of the density of pest population reaching to RMn is.
Figure 6.
The effects of the spraying M of pesticide in each generation on the threshold value RMn. The parameters value are fixed as follows: r=0.4, d1=0.6, h=0.75, p0=0.0001.
From Figure 6, we can also see that the density of pest population will reach to the threshold after several times of spraying pesticide, due to the development of pesticide resistance. Therefore, in order to eradicate pest population, the alternative choice is to switch another pesticide after the using of one pesticide for several times. In the following, we will discuss the optimal switching time.
Note that, in order to eradicate the pests population, the threshold value RMn should below one for all n=0,1,2,⋯. Therefore, it's necessary to switch the pesticides before the threshold value RMn reach to one. Here, we assume that the threshold value reach or exceed to 1 firstly after pest control in n3th generation, i.e..
n3=max{n:RMn≤1},
and the optimal generation for switching pesticides is n3. In order to determine n3 analytically, we let RMn=1, that is
The detailed calculation of the pn3 is provided in Appendix B. We substitute pn3 into Eq (2.5) or Eqs (3.10)–(2.10), and we can obtain the optimal switching time n3 under different cases.
In the following, we address how the xn varies as the parameters τ1 and T change, which are quite important for pesticide applications. Firstly, by induction, we can get the recursion formula for xn of Eq (4.3) as follows:
From Eq (4.7) we can see that xn is a decreasing function with respect to τ1 and T, which means that the longer of period or the later of pesticide spraying is, the more benefit to pest control.
4.2. Switching pesticide with EIL as a guide
In this subsection, we focus on the control tactics of EIL. That is farmers should control pest when the density of pest population reach to EIL. As the former states, because of the resistance of pesticide, spraying one type of pesticide could not maintain the density of pest population below the EIL. Thus after some times of one type of pesticide spraying, farmers should switch another type of pesticides.
We assume that after the n4th generation, farmers should switch another type of pesticide, which means that xn4≤EIL and xn4+1>EIL, that is, the optimal switching generation is n4+1. In order to find the n4, we let xn4+1>EIL. From Eq (4.3), we have
There are many factors to cause the resistance of pest to pesticide. The main factors are the external factor (i.e. the high frequency and large doses spraying of pesticides) and the genetic factors. Consider the above two factors, we set up the evolution equations of pesticide resistance under one times spraying pesticide in one generation or multiple spraying pesticide in one generation, and introduce the equation into pest control models.
Due to the development of pesticide resistance, the long-term use of the same kind of pesticides to control pests, farmers cannot reach the aim of pest control, however, the pest population should be outbreak again. In order to control pest population, farmers usually need to switch pesticides in some kind of pesticides. In this work, we study the threshold condition to eradicate pest population under one times spraying pesticide in one generation, analyze the relationship of the threshold condition and evolution of pesticide resistance. Moreover, we get the maximum number of one type of pesticide sprayings, and optimal switching time of pesticide. In the aim of controlling pest population below the EIL, we also analyze the optimal switching time of pesticide under the case of one times spraying pesticide in one generation. Farmers usually control pest population many times in one generation, under this case, we research the optimal switching time of pesticide with the aim of eradicating pest population and controlling pest population below the EIL, respectively.
6.
Discussions
In this study, by assuming that the pest resistance to pesticide is determined by a single gene with two alleles R and S and according to the genetic laws, we developed a novel model for pest resistance to pesticide with external induced resistance and genetic resistance describing the dynamics of the development of the pesticide resistance. With this model, we investigated the impact of the death rate of susceptible pests and the spraying times of pesticide in each generation on the frequency of the resistance allele. We showed that when R is completely recessive gene or completely dominant gene, decreasing the death rate of susceptible pests and the spraying times of pesticide in each generation can help to decrease the frequency of the resistance allele.
In practice, pest control, including spraying pesticide and releasing the natural enemies are usually implemented impulsively. Therefore, many mathematical models with impulsive chemical control by spraying the pesticide and natural enemies have been proposed and deeply studied [38,39,40,41,42,43,44,45]. In theses studies, they usually assumed that the chemical and biological control were implemented at the beginning at the end of one generation. However, pests usually have non-overlapping generations, which indicates that control methods should be taken within each generation. In this study, we incorporate the impulsive control within each generation into a discrete population model. Through the analytical methods, we then drived a novel model based on the continuous Logistic model with both single pesticide applications and the evolution of pest resistance to pesticide. Based on these models, we investigated the effects of the timing of pesticide application on the density of pest population by calculating iteration equation. Our theoretical analyses reveal that the later the pesticide was spraying, the smaller the density of the pests is. Further, we extended a discrete pest population growth model by including both the multiple instantaneous pesticide applications within each generation and the evolution of pest resistance to pesticide. Finally, we provided a threshold condition for pest eradication, and based on the threshold condition we discussed the optimal generation when different types of pesticides were used with a switching regime. With the aim of controlling the density of the pest population below EIL, we provided a switching strategy guided by EIL, where the optimal generation for switching another pesticides was investigated.
Note that, biological control by releasing the natural enemies, as an important component of the IPM, helps to decrease the pest and slow down the development of the pesticide resistance. It remains challenging how to combine the biological to chemical control aiming at fighting against the development of pesticide resistance, and what the optimal releasing rate of the natural enemies should be. This was left for our future works.
Acknowledgments
This work was supported by the National Natural Science Foundation of China (NSFCs 11871319, 11631012).
In order to solve equation f(pn)=0, we analyze the equation f(x)=0 from the following cases:
Case (A1): Cd1>0 (i.e. 0<d1<1−e−r).
In this case, we can easy to see that f(0)>0.
If Ah,d1>0, then f(x)>0 for all 0≤x≤1.
If Ah,d1≤0, we can easily see that Bh,d1>0 (due to Cd1>0), then f(x)>0 for all 0≤x≤1.
thus, f(pn)>0 (0<pn≤1).
Case (A2): Cd1<0 and Ah,d1≠0.
For this case, f(0)=Cd1<0 (i.e 1−e−r<d1<1), the equation f(pn)=0 has solution pn1=−Bh,d1+√B2h,d1−4Ah,d1Cd12Ah,d1
Case (A3): Cd1<0 and Ah,d1=0.
For this case, the equation f(x)=0 turns to f(x)=Bh,d1x+Cd1=0. Due to f(1)>0 and f(0)<0, then the equation f(pn)=0 has solution pn1=−Cd1Bh,d1.
Case (A4): Cd1=0 (i.e. d1=1 or d1=1−e−r).
If d1=1, then
Ah,d1=2h(e−r−h)+1−e−r,
Bh,d1=2h(h−e−r).
If h≥e−r, then Bh,d1≥0, we can easy to see that f(pn)>0 for all 0<pn≤1; If h<e−r, then Bh,d1<0 and Ah,d1>0, then then the equation f(pn)=0 has solution pn1=−Bh,d1Ah,d1.
If d1=1−e−r, then
Bh,d1=2h(1−e−r)(h(1−e−r)+e−r)>0,
for this case, we can easy to see that f(pn)>0 for all 0<pn≤1.
due to a(M+1)1+b(M+1)1+c(M+)1=a(1)1+b(1)1+c(1)1=1.
Using the same methods as in the proof of Appendix A, we analyze the equation g(x)=0 from the following cases:
Case (B1): CMd1>0 (i.e. 0<d1<1−e−rM).
In this case, we can easy to see that BMh,d1>0 due to (M+1)(1−d1)M−e−r>0 for all 0<d1<1−e−rM and ∑M+1i=2(2(hd1)iCiM+1(1−d1)M+1−i)>0. Thus, g(x)>0 (0≤x≤1) for all 0<d1<1−e−rM.
Case (B2): CMd1<0 and AMh,d1≠0.
For this case, g(0)=CMd1<0 (i.e 1−e−rM<d1<1), the equation g(x)=0 has solution pn3=−BMh,d1+√BMh,d12−4AMh,d1CMd12AMh,d1.
Case (B3): CMd1<0 and AMh,d1=0.
For this case, the equation g(x)=0 turns to g(x)=BMh,d1x+CMd1=0. Due to g(1)>0 and g(0)<0, then the equation g(pn)=0 has solution pn3=−CMd1BMh,d1.
Case (B4): CMd1=0 (i.e. d1=1 or d1=1−e−rM).
In this case, if d1=1, then AMh,1=−2hM+1+2he−r+1−e−r and BMh,1=2h(hM−e−r). It is easy to know that AMh,1+BMh,1>0. If h≥e−rM, then BMh,1≥0, we can easily know that g(x)>0; If h<e−rM, then BMh,1<0 and AMh,1>0, thus, we have g(pn3)=0 with pn3=−BMh,d1AMh,d1.
for this case, we can easy to see that g(pn)>0 for all 0<pn≤1.
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Figure 1. Schematic diagram for the systems (2.1) and (4.1). Here, purple lines represent the impacts of social media advertisements on making literate/illiterate people aware about the disease whereas blue color corresponds to the seasonal variation in the growth rate of social media advertisements
Figure 2. Intersections of isoclines (3.5) and (3.6). Here, green and red colors represent the isoclines (3.5) and (3.6), respectively. Parameters are at the same values as in Table 2
Figure 3. Normalized forward sensitivity indices of R0 with respect to Λ, ν, α, d, β1, β2, λ1, λ2, γ, λ0 and T0. Parameters are at the same values as in Table 2 except λ2=0.012, α=0.02, p=500 and λ0=0.00005
Figure 4. Effect of uncertainty of the model (2.2) on infected population. Baseline values of parameters are given in (5.2)
Figure 5. Plot of R0 with respect to (a) T0 and λ1, and (b) T0 and λ2. Rest of the parameters are at the same values as in Table 2 except λ1=0.04 in (b)
Figure 6. Contour line representing the equilibrium value of infected population, Y(t), as functions of (a) r and r0, (b) λ1 and p, (c) λ2 and p, and (d) T0 and λ0. Rest of the parameters are at the same values as in Table 2
Figure 7. Effects of social media advertisements on the equilibrium level of infective population. Parameters are at the same values as in Table 2 except λ1=0.01
Figure 8. Bifurcation diagram of system (2.2) with respect to r. Limit cycles arising in Y−Xa plane on increasing the value of r. Rest of the parameters are at the same values as in Table 2
Figure 9. Bifurcation diagram of system (2.2) with respect to λ1. Rest of the parameters are at the same values as in Table 2 except r=0.05
Figure 10. Bifurcation diagram of system (2.2) with respect to T0. Rest of the parameters are at the same values as in Table 2 except λ0=0.004 and α=0.002
Figure 11. System (4.1) exhibits periodic solution at r=0.015. Rest of the parameters are at the same values as in Table 2, r11=0.01 and ω=2π/365
Figure 12. Global stability of (a) equilibrium E∗ of systems (2.2) and (b) positive periodic solution of system (4.1). Parameters are at the same values as in Table 2 except in (a) λ1=0.0003 and λ2=0.00002, and (b) r=0.015, r11=0.01 and ω=2π/365. Figures show that solution trajectories starting from different initial points ultimately converge to the equilibrium E∗ in (a) and a unique positive periodic solution in (b)
Figure 13. System (4.1) exhibits higher periodic solution at r=0.03. Rest of the parameters are at the same values as in Table 2, r11=0.01 and ω=2π/365