Assessing the Impact of Psyllid Pesticide Resistance on the Spread of Citrus Huanglongbing and Its Ecological Paradox
Abstract
:1. Introduction
2. Materials and Methods
- We assume that the replanting rate is determined by the abundance or density of plants, using and to describe the logistic growth of healthy and infected plants, respectively. In these equations, r represents the intrinsic growth rate of healthy plants, () denotes the proportional reduction in the replacement rate for infected plants, and K is the maximum capacity for planting citrus trees in the orchard;
- The forces of infection for HLB transmission, namely the infection rates, are defined as follows: represents the vector-to-host transmission rate, while represents the host-to-vector transmission rate, where is the transmission probability from infectious ACP to susceptible citrus trees, and is the transmission probability from infectious citrus trees to susceptible ACP. Additionally, the natural mortality rate of citrus trees is given by , and the roguing rate of infected citrus trees is represented by ;
- It is assumed that mating among adult ACPs (between individuals of opposite sexes) occurs randomly [16]. In other words, all adult ACPs have an equal chance of reproducing and mate with any other adult ACP of the opposite sex with the same probability. The presence or absence of insecticide resistance is determined by a pair of alleles in the ACP population, which in turn affects the parameters for ACP mortality and growth rates. The insecticide-sensitive allele is denoted by S, and the insecticide-resistant allele by R. Thus, following the idea outlined in [16,19], we take the frequency of each allele using the following formulas:
- Note that ACP insecticide resistance is inherited (vertically) [16,20]; that is, an insecticide-resistant adult ACP produces insecticide-resistant offspring. Susceptible ACPs of all genotypes (, , and ) acquire HLB infection at a rate of . ACPs of the -genotype ( and ) experience natural mortality at a rate of , as well as additional mortality due to insecticide use at a rate of ;
- It is further assumed that there is a mortality fitness cost associated with both homozygous resistant and heterozygous ACPs [21,22,23]. Specifically, ACPs of the genotype experience natural mortality at a rate of (with reflecting the increased mortality rate of genotype ACPs due to the fitness cost, compared to the natural mortality rate of genotype ACPs). ACPs of the genotype suffer natural mortality at a rate of (where represents the increased mortality rate of genotype ACPs due to the fitness cost, compared to genotype ACPs). Note that if the resistant allele (R) is dominant, and if the R allele is recessive;
- The population of ACPs with the genotype decreases due to insecticide use at a rate of . Similarly, the population of genotype decreases at a rate of , where is a modification parameter that accounts for the assumed decrease in mortality rate of genotype vectors due to insecticides, compared to genotype vectors (due to the mortality fitness cost). Additionally, genotype vectors experience mortality from insecticide use at a rate of , where is a modification parameter that reflects the degree of dominance of the resistant allele (i.e., models the case where the resistant allele is dominant, while represents the scenario when it is recessive). The parameter of the resistant allele measures the relative impact of the heterozygote compared to the two corresponding homozygote genotypes, and (see [18]).
3. Model Analysis
3.1. Basic Properties
3.2. Existence of Disease-Free Equilibria
- (i)
- and ;
- (ii)
- and ;
- (iii)
- and , provided that ;
- (iv)
- any value in with , provided that
- (1)
- The NTSDFE () exists if and only if ;
- (2)
- The NTRDFE () exists if and only if ;
- (3)
- The NTCDFE () exists if and only if and , or if and only if and
- (i)
- If , then , and ;
- (ii)
- If , then , and ;
- (iii)
- If , then , and ;
- (iv)
- If , then , and .
3.3. Local Asymptotic Stability of Equilibria
- (a)
- When or and , the NTCDFE is locally asymptotically stable if and unstable if .
- (b)
- When , the NTSDFE is locally asymptotically stable if and unstable if ;
- (c)
- When , the NTRDFE is locally asymptotically stable if and unstable if ;
- (d)
- The TDFE is always locally asymptotically stable.
3.4. Global Asymptotic Stability of Equilibria
- (a)
- If or , then the set is positively invariant provided that and .
- (b)
- If and , then the set is positively invariant.
- (c)
- If and , then the set is positively invariant.
- (a)
- When or , the NTCDFE () is globally asymptotically stable in if , and .
- (b)
- If , and , then the NTSDFE () is globally asymptotically stable in .
- (c)
- If , and , then the NTRDFE () is globally asymptotically stable in .
4. Global Sensitivity Analysis of the Reproduction Threshold
5. Numerical Simulation
6. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
References
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Variable | Description |
Population of susceptible citrus trees | |
Population of infected citrus trees | |
Population of susceptible sensitive ACP | |
Population of infected sensitive ACP | |
Population of susceptible resistant ACP | |
Population of infected sensitive ACP | |
Population of susceptible sensitive ACP | |
Population of infected resistant ACP | |
Parameter | Description |
K | Environmental carrying capacity of citrus trees |
Recruitment rate of citrus trees | |
Transmission probability from infected ACP to susceptible citrus trees | |
Natural mortality rate in citrus trees | |
Probability that a diseased citrus trees sapling is not removed | |
The roguing rate of infected citrus trees | |
Recruitment rate of ACP | |
m | Average carrying capacity of ACP per citrus tree |
Transmission probability from infected citrus trees to susceptible ACP | |
Natural mortality rate of ACP | |
Death rate due to the (encounter with) insecticides for genotype ACP | |
Modification parameter in natural mortality rate of genotype ACP due to fitness cost in comparison to the natural mortality rate of genotype ACP | |
Modification parameter in natural mortality rate of genotype ACP due to fitness cost in comparison to the natural mortality rate of genotype ACP | |
Modification parameter in death rate of genotype ACP due to the insecticides in comparison to the death rate of genotype ACP | |
Modification parameter in death rate of genotype ACP due to the insecticides in comparison to the death rate of genotype ACP |
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Gan, R.; Luo, Y.; Gao, S. Assessing the Impact of Psyllid Pesticide Resistance on the Spread of Citrus Huanglongbing and Its Ecological Paradox. Computation 2024, 12, 242. https://doi.org/10.3390/computation12120242
Gan R, Luo Y, Gao S. Assessing the Impact of Psyllid Pesticide Resistance on the Spread of Citrus Huanglongbing and Its Ecological Paradox. Computation. 2024; 12(12):242. https://doi.org/10.3390/computation12120242
Chicago/Turabian StyleGan, Runyun, Youquan Luo, and Shujing Gao. 2024. "Assessing the Impact of Psyllid Pesticide Resistance on the Spread of Citrus Huanglongbing and Its Ecological Paradox" Computation 12, no. 12: 242. https://doi.org/10.3390/computation12120242
APA StyleGan, R., Luo, Y., & Gao, S. (2024). Assessing the Impact of Psyllid Pesticide Resistance on the Spread of Citrus Huanglongbing and Its Ecological Paradox. Computation, 12(12), 242. https://doi.org/10.3390/computation12120242