1. Introduction
Huanglongbing (HLB), formerly termed citrus greening disease, is a devastating and highly contagious plant pathology caused by
Candidatus Liberibacter species. This pathogen inflicts systemic damage to citrus phloem tissues, manifesting as severe chlorosis, fruit deformities, and premature abscission, ultimately leading to catastrophic declines in both yield and fruit quality. Since its initial detection in China, HLB has emerged as a persistent biosecurity threat, inflicting substantial economic losses across global citrus-producing regions [
1]. Despite decades of research, effective curative measures remain elusive, cementing HLB’s status as one of the most intractable challenges in contemporary phytopathology.
The Asian citrus psyllid (
Diaphorina citri), a hemipteran insect within the
Psyllidae family, serves as the sole natural vector for HLB transmission [
2]. This oligophagous pest preferentially colonizes
Rutaceae hosts, including citrus (
Citrus spp.), orange jasmine (
Murraya paniculata), and Chinese boxthorn (
Lycium chinense), with feeding activities concentrated on emerging flush growth. Intriguingly, Mann et al. [
3] demonstrated that HLB-infected plants undergo transcriptomic reprogramming, resulting in altered volatile organic compound profiles and visual cues (e.g., leaf yellowing). These pathogen-induced modifications enhance host attractiveness to
D. citri, thereby creating a positive feedback loop that amplifies vector recruitment and oviposition on infected hosts.
Current HLB management strategies rely heavily on the prompt elimination of symptomatic trees. Although linear removal rate functions have been conventionally employed in epidemiological models [
4,
5,
6], such approaches inadequately capture real-world operational constraints. Drawing inspiration from [
7]’s saturation-dependent therapeutic framework, this study introduces a nonlinear removal function,
where
denotes the baseline removal rate and
quantifies delayed intervention effects. This formulation reflects two critical regimes: (1) at low infection intensities, removal approximates linear dynamics (
); (2) at large infection scales, removal plateaus at
, mirroring saturation effects from finite resources (e.g., labor shortages, budgetary limitations). Notably, setting
recovers the classical linear model, enabling direct comparison with prior studies.
Spatiotemporal heterogeneity constitutes a pivotal yet underexplored dimension in HLB epidemiology. Although temporal models dominate the literature [
8,
9], the spatial dispersal capacity of
D. citri, particularly adult psyllids’ ability to traverse kilometers via wind-aided flight, demands integration of diffusion dynamics. Orchards rarely exist as isolated systems; rather, pathogen–vector interactions operate across interconnected agricultural landscapes where microclimatic variations and anthropogenic activities modulate transmission thresholds. A spatially explicit modeling framework thus offers critical insights into how geographic disparities in resource allocation, surveillance efficacy, and vector mobility influence epidemic trajectories.
The dissemination of diseases is affected by both temporal and spatial factors. As a result, the spatial aspect of infectious disease models has attracted substantial interest. This focus has led to remarkable outcomes in epidemiology and ecology, and these models have been successfully applied in practical disease prevention and control measures [
8,
9]. Given that the Asian citrus psyllid has a certain flight capacity, adult psyllids are capable of dispersing between orchards through near-ground strong winds. Developing an HLB transmission model that incorporates spatial diffusion terms can more accurately represent the influence of spatial heterogeneity on disease spread.
This paper is structured as follows:
Section 2 formulates a non-spatial compartmental model incorporating infected-tree removal and vector preference dynamics.
Section 3 rigorously analyzes system equilibria, derives the basic reproduction number (
), establishes global stability criteria, and examines bifurcation behavior at
.
Section 4 extends the model through diffusion operators to investigate pattern formation and Turing instability in spatial systems.
Section 5 validates theoretical predictions via numerical simulations, and
Section 6 synthesizes key findings and their implications for integrated pest management.
2. Model Formulation
Based on compartment modeling principles, we classify citrus trees into two epidemiological states: susceptible () and infected (). Similarly, the psyllid vector population is partitioned into susceptible () and infected () categories. denotes the total number of citrus trees in the orchard at time t, such that . Likewise, denotes the total number of psyllids in the orchard at time t, with .
A critical behavioral factor in HLB transmission is the preferential feeding tendency of psyllids toward infected citrus trees. Field observations suggest that infected trees emit distinct volatile organic compounds (VOCs) which act as olfactory cues, attracting adult psyllids to settle and feed more frequently on
hosts compared to
hosts. To quantify this behavior, we introduce
w as the preference coefficient, defined as the ratio of psyllid visitation probability to infected versus susceptible trees. Specifically, if
, psyllids exhibit a stronger attraction to infected trees; if
, psyllids avoid infected trees, and if
, no preference exists (equal visitation rates). Building on the known tropic behavior of psyllids, this paper assumes
. Consequently, the force of infection for citrus trees is modulated by
w, such that the effective contact rate between infected psyllids (
) and susceptible trees (
) follows a standard style:
where
is the transmission rate between infected psyllids and susceptible citrus trees. Similarly, the force of infection for psyllids is
where
is the transmission rate between susceptible psyllids and infected citrus trees.
Considering the operational constraints imposed by limited human resources and economic capacities in agricultural management, we reasonably assume that disease containment measures exhibit a saturation effect when dealing with large-scale infections. This motivates the adoption of a saturated removal rate formulated as
where
represents the maximum theoretical removal rate under ideal resource conditions and
quantifies the delayed response intensity caused by logistical constraints, with larger
values indicating stronger suppression of removal efficiency at high infection levels. The denominator term (
) introduces a density-dependent inhibition mechanism, reflecting the reality that removal efficiency decreases proportionally as infected citrus tree density (
) increases. This aligns with Michaelis–Menten-type saturation kinetics observed in biological systems [
10].
Further, we assume that the orchardist employs an “immediate replanting” strategy, thereby maintaining a constant total number of citrus trees, denoted by
K. Based on the above assumptions, we establish a HLB transmission model with saturated removal rates and psyllid bias:
where
d is the natural mortality rate of citrus trees,
is the constant recruitment rate of psyllids and
u is the mortality rate of psyllids, including natural mortality and mortality caused by pesticide spraying. We also assume that all parameters of the model are positive.
Given that the life cycle of citrus psyllids is significantly shorter than that of citrus trees, the psyllid-related subsystem will swiftly converge toward an equilibrium state. Consequently, the dynamic characteristics of system (
1) can be simplified by analyzing its limiting system. It follows from system (
1) that
for all
, and
. Thus, the limit system of system (
1) yields
The flowchart depicting the transmission dynamics of citrus HLB is presented in
Figure 1. The parameters and their biological significance in model (
2) are summarized in
Table 1.
It is evident that
is the positively invariant set of system (
2).
4. Stability and Bifurcation of Spatial System
Building on the discussion in the previous section, we introduce the model with homogeneous Neumann boundary conditions in this section, as detailed below.
where
denotes the Laplace operator,
and
denote the diffusion of infected citrus trees and infected psyllids, respectively,
denote the corresponding diffusion coefficients,
denotes the bounded region with a smooth boundary in
, and
n is the outward unit normal vector on
. Based on the realistic background, the spread of citrus trees is negligible compared to the spread of psyllids. Therefore, it is reasonable to assume that
.
The aim of this section is to investigate the dynamical properties of the spatial system (
9). This includes analyzing the stability of its equilibria and elucidating the reasons for the absence of complex dynamical behavior within the system.
Theorem 7. The disease-free equilibrium of system (9) is locally asymptotically stable if , and it is unstable if . Proof of Theorem 7. The linearized equation of system (
9) at the disease-free equilibrium
is given by
Accordingly, the characteristic equation associated with
is
As in [
13], we denote the eigenvalue of
on
under a homogeneous Neumann boundary condition as
, where
.
According to the Hurwitz criterion, we have
Note that and for all , provided that . Hence, according to the Routh–Hurwitz criterion, is locally asymptotically stable provided that . The proof is complete. □
Theorem 8. If the equilibria of system (9) exist, then is unstable, and is locally asymptotically stable. Proof of Theorem 8. The linearized equation of model (
9) at the equilibrium
is given by
The Jacobian matrix of the spatial system (
9) evaluated at the equilibrium
is
where
The characteristic equation is
where
From (
11), we derive that the characteristic equation at the equilibrium
is
In view of the Hurwitz criterion, we have
For all , the inequalities and are satisfied. Consequently, the characteristic roots have negative real parts, indicating that the equilibrium is locally asymptotically stable. This completes the proof. □
Remark 1. Note that for every , both and are positive. As a result, the spatial system (9) does not exhibit complex dynamical phenomena such as Hopf bifurcation, Turing–Hopf bifurcation, or Turing instability at the equilibrium . 5. Numerical Simulations
In the previous section, we analyzed the distribution and bifurcations of equilibrium types and quantities for system (
2), deriving key conclusions. This section validates these findings using MATLAB
® R2023a simulations. Below, we outline the parameters required for verification.
We first outline parameter selection. Based on ref. [
14], we adopt a standard planting density of 4 m row spacing and 2.5 m column spacing for citrus trees. For a 5-hectare orchard, the total number of trees is approximated as
. Grafted citrus trees typically bear fruit 3–4 years after transplantation, with a commercial lifespan of 15–20 years. We assume 18 years, yielding a monthly natural elimination rate of
. For citrus psyllids, the average lifespan is 2.5 months [
6,
15], giving us a mortality rate of
. Other parameter values used were
,
,
,
, and
, from which we calculated
.
The regional distribution of equilibria in system (
2) as functions of
and
is shown in
Figure 2. The red region denotes the absence of endemic equilibria, the green region indicates the coexistence of two endemic equilibria, and the blue region signifies the presence of a unique endemic equilibrium. The red dotted curve delineates the critical threshold
, representing the epidemic boundary for the parameter pair
.
As the basic reproduction number serves as a critical epidemiological threshold, we construct a bifurcation diagram in the parameter plane to characterize system dynamics. To comprehensively illustrate bifurcation types, we select two distinct values for the parameter : and .
When
, system (
2) undergoes backward bifurcation at
(
Figure 3). In the sub-threshold regime (
), three coexisting equilibria emerge: a stable disease-free equilibrium and two endemic equilibria (one stable, one unstable). This bistability is further characterized by an additional critical threshold
, identified through saddle-node bifurcation analysis. The hysteresis loop between
and
implies three key insights: (i) Temporary control measures that reduce
below 1 but may fail to achieve permanent eradication above 0.703. (ii) Long-term HLB persistence can occur even with
due to the basin stability of the endemic state. (iii) Eradication requires a sustained intervention to push
, thereby breaking the basin of attraction for the endemic equilibrium.
In contrast,
Figure 4 demonstrates that system (
2) exhibits a forward bifurcation at
, when
. In this regime, no endemic equilibrium exists for
, confirming
as an absolute eradication threshold for HLB. This indicates that maintaining
through a continuous reduction of secondary infections guarantees disease elimination.
Next, we analyze how the basic reproduction number responds when the vector preference parameter and the removal rate of infected trees are altered simultaneously. As shown in
Figure 5,
increases with an ascending value of the preference parameter
or a descending value of the removal rate
. The red line denotes the threshold where
, while the distinct colors (ranging from blue to yellow in two-step increments) illustrate
values increasing from 0 to 11. These results highlight that both the preference behavior of psyllids and the control strategy of removing infected trees play key roles in HLB management.
Figure 6 displays the spatiotemporal sequence plots of system (
9). With parameter settings
, and
,
, showing the disease will be eradicated (see
Figure 6a,b). Conversely, when
,
, indicating the disease will become endemic (see
Figure 6c,d). These results validate the conclusions of Theorem 7.
6. Conclusions and Discussion
This study advances our understanding of HLB transmission dynamics by integrating two critical, yet previously underexplored, factors into a compartmental model: saturated removal rates of infected trees and vector behavioral bias. The incorporation of saturated removal rates reflects real-world limitations in detecting and eliminating infected trees. Unlike linear removal assumptions in prior models, saturation acknowledges that delayed interventions (e.g., due to diagnostic lag or resource constraints) allow infections to accumulate nonlinearly, amplifying outbreak risks. Simultaneously, vector behavioral bias, i.e., the preferential movement of psyllids toward infected trees, captures a key ecological feedback loop: infected hosts attract more vectors, accelerating pathogen spread. Together, these mechanisms explain why traditional models, which neglect these factors, may underestimate HLB’s persistence and resurgence potential.
Next, we will systematically review the main theoretical research achievements of this paper and deeply explore the guiding significance and practical implications of these theoretical insights for actual disease management.
The basic reproduction number is a cornerstone for predicting outbreak thresholds. However, our analysis reveals the following dynamic behavior. (i) Subcritical Bistability (): When falls below 1, the system can exhibit bistability, where both disease-free and endemic equilibria coexist. This implies that even if is suppressed below the canonical threshold, pre-existing infections or transient vector surges could trigger outbreaks. (ii) Supercritical Uniqueness (): When exceeds 1, the system converges to a unique endemic equilibrium, independent of initial conditions. This aligns with the classical epidemic theory. Therefore, eradication requires not only reducing but also managing initial infection loads to avoid bistable traps.
Delayed removal triggers backward bifurcation: Conversely, slow removal of infected trees () induces backward bifurcation, creating a subcritical threshold () where endemicity persists even with . This mirrors challenges in managing diseases like tuberculosis, where delayed diagnosis undermines containment. Consequently, rapid removal of infected trees () is non-negotiable when the aim is to avoid backward bifurcation’s destabilizing effects.
Contrary to initial expectations, reaction–diffusion processes did not alter equilibrium stability in our analysis. This finding suggests that homogeneous mixing assumptions may adequately characterize HLB spread at regional scales, implying that simplified models without explicit spatial dynamics could still capture key transmission mechanisms. Notably, spatial heterogeneity appears to play a secondary role compared to temporal factors, like the delayed removal of infected trees, which have been shown to significantly influence bistability and outbreak thresholds.
While reaction–diffusion dynamics did not impact equilibrium stability in the current model, future research could explore how spatial heterogeneity, such as variability in orchard layouts or seasonal psyllid migration patterns, might modulate disease spread under different management scenarios. By integrating these dynamical principles into agricultural practices, stake holders can develop more targeted strategies to mitigate HLB’s devastating impact on citrus production.