This is an uncorrected proof.
Figures
Abstract
Modeling vector-borne pathogens that circulate among several host and vector species hinges on how the force of infection (FOI) is defined. In an i‐host, j‐vector susceptible-infectious-recovered modeling framework I compare two common FOI denominators: (i) a weighted form in which vectors bite preferred hosts disproportionately, and (ii) an unweighted form that assumes opportunistic biting. Using identical parameter sets calibrated to primate–Aedes data from Kédougou (Senegal), the weighted FOI doubles the basic reproduction number (R0) relative to the opportunistic FOI and can shift R0 across the epidemic threshold. It also produces higher long-run prevalence and larger oscillations. Both autonomous formulations undergo a forward transcritical bifurcation at R0 = 1. Selecting an ecologically realistic biting assumption is therefore critical for predicting sylvatic-to-urban spillover risk and designing interventions in multi‐host systems.
Author summary
Mosquito-borne diseases such as dengue and yellow fever circulate in forests where several mosquito and animal species interact. I wanted to know how much it matters which host a mosquito decides to bite. Using a model that follows a virus moving among two monkey species and two mosquito species, I tested two scenarios on either end of the behavioral range: mosquitoes that “home in” on their preferred host, and mosquitoes that bite whatever is most abundant.
Simply swapping this one behavioral assumption changed several model predictions. Targeted biting doubled the basic reproductive number in the baseline comparison, shifted the epidemic threshold, and produced higher long-run prevalence and larger oscillations. Opportunistic biting produced lower transmission and more strongly damped dynamics. Because these differences arise from the FOI formulation, field studies that measure real biting patterns are crucial for forecasting spillover into people and for deciding whether to focus on reducing certain hosts or controlling mosquito numbers.
By uniting ideas from biodiversity (“dilution effects”) and mosquito choice, my work offers practical guidance for researchers and health agencies working in multi-host disease systems.
Citation: Althouse BM (2026) Ecological specialization in vectors alters transmission thresholds and endemic dynamics in multi-host, multi-vector systems. PLoS Comput Biol 22(9): e1014754. https://doi.org/10.1371/journal.pcbi.1014754
Editor: Natalia L. Komarova, University of California Irvine, UNITED STATES OF AMERICA
Received: May 12, 2025; Accepted: August 22, 2026; Published: September 11, 2026
Copyright: © 2026 Benjamin M. Althouse. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: Code to run simulations and recreate figures is in a Github repository, available at https://github.com/althouse/Althouse_Vector_Ecological_Specialization
Funding: This work was partially funded by NIH grant AI069145. Additional funding was from an NSF Graduate Research Fellowship (grant no. DGE-0707427), the Santa Fe Institute, the Omidyar Group, and Bill and Melinda Gates through the Global Good Fund to BA. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: I have read the journal’s policy and the authors of this manuscript have the following competing interests: I am a current employee of, and own stock in, Pfizer, Inc. Pfizer had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
1 Introduction
Pathogens exist in a world populated by many potential hosts and vectors. While evolution has directed many pathogens to specialize and infect a single or few hosts, other pathogens can infect a number of varied hosts and vectors [1–4]. Malaria [5], dengue virus [6–8], yellow fever virus [9], chikungunya virus [10,11], Rift Valley fever virus [12], West Nile virus [13], and Zika virus [7,11,14–17] all cause major morbidity and mortality worldwide and have transmission dynamics dictated by multiple host and vector species. While a recent systematic review reveals an accelerating shift toward multi-host formulations in West Nile Virus (WNV) [18], little consensus has been reached on the appropriate formulation of the host-vector model structure, and the majority of mathematical models describing vectored pathogen transmission focus on a single host and vector [19,20].
Many studies in disease ecology show that adding host species to a community can either amplify or reduce disease transmission [21]. This effect depends on each host’s competence and the vector’s feeding behavior. When host diversity reduces transmission, this is known as the dilution effect. Conversely, when additional hosts increase transmission – because they are highly competent or boost vector abundance – this is called amplification [22]. Alternate hosts can divert vectors from primary hosts (zooprophylaxis), or, if highly competent, they may increase transmission. These ecological dynamics underscore the importance of how the transmission term is represented in a multi-host disease model.
The force of infection (FOI), or transmission term, in mathematical models of disease dynamics dictates the rate of contact between susceptible and infectious hosts and vectors, incorporating the transmission potential of a pathogen [23]. Importantly, the transmission term feeds into the calculation of the basic reproductive number, R0, defined as the number of secondary cases caused by an infected individual in an entirely susceptible population [24]. It has been previously shown that different forms of the transmission term in host–vector models, often assumed to produce equivalent predictions, can give rise to conflicting predictions of disease dynamics [25]. In practice, this means that two models of the same system might reach opposite conclusions about whether an outbreak will occur, posing a challenge for public health planning.
Recent studies further highlight the importance of capturing host–vector heterogeneity. For example, Ross River virus (a multi-host, multi-vector arbovirus) is found in Australia, Papua New Guinea, and the islands of the South Pacific, and exhibits distinct transmission cycles driven by specific mosquito–host interactions. A 2021 analysis found that certain mosquito–bird pairs sustain an enzootic cycle of Ross River virus, whereas other mosquito–human pairs drive urban spillover, underscoring the role of particular host–vector combinations in transmission [26]. A growing body of literature has established that assumptions regarding disease transmission can generate conflicting predictions, and systematic reviews show that a significant fraction of models now deviate from classical mass-action assumptions to better capture ecological realities. Building on this, this work quantifies how innate vector feeding selectivity, when formalized in the force-of-infection term, changes transmission thresholds, long-run prevalence, and transient dynamics in a multi-host, multi-vector system. Similarly, theoretical work has shown that explicitly including vector host preference and host competence in a two-host model can determine whether adding a secondary host leads to a dilution or an amplification of disease risk [27]. These examples illustrate that host community composition and vector behavior can fundamentally shape pathogen spread.
At root, the two biting formulations I examine embody different causal narratives about what limits mosquito-host contact. The frequency-dependent (vector-limited) framework starts from the mosquito’s perspective: the pool of bites is fixed by mosquitoes’ physiological capacity for blood feeding, and hosts merely divide that finite resource among themselves. In contrast, the density-dependent (host-limited) framework is written from the host’s perspective: each host presents an independent “surface” that can, in principle, receive an unlimited number of probing attempts, so aggregate biting scales with the sum of host availabilities unless an explicit denominator is imposed. Normalizing the density-dependent expression by the weighted host total makes the two equations algebraically identical, but it does not erase this conceptual distinction: the first treats mosquito search effort as the bottleneck, the second treats host encounter probability as the bottleneck. Because the biological processes that control transmission (e.g., resting-site limitation versus host defensive behavior) differ between systems, the choice of framework is not merely a matter of prey specificity: it encodes our assumption about which side of the interaction is limiting and therefore dictates how new data (such as changes in vector abundance, host diversity, or feeding interruption rates) should be mapped onto model parameters.
In the following sections, I use a general modeling framework to examine two contrasting assumptions about mosquito host choice and their epidemiological consequences. I demonstrate how differences in multi-host, multi-vector pathogen model transmission terms correspond to distinct biological scenarios and lead to conflicting epidemiological predictions.
2 Methods and results
2.1 Mosquito host choice
There remains an open question whether vectors have strong innate preferences for particular hosts, or alternatively if vectors merely feed on whichever hosts are nearby and available. Several factors influence mosquito behavior, including temperature, humidity, and odors [28], which can guide host seeking and potentially create apparent host preferences. Carbon dioxide mediates both long- and short-range host seeking: long-range attraction is driven by CO2 and other organic molecules emitted from host skin, breath, and excreta [29]. Mosquito genetics may also influence individual host choice, as host attraction varies across vector and host species [30]. Environmental conditions, including temperature and humidity, can further modulate mosquito activity and host-seeking behavior [31].
Several studies have indicated the importance of host characteristics in mosquito host choice. For example, anthropometry is associated with more frequent biting for both Anopheles [32] and Aedes mosquitoes [33]. Additionally, host defensive behavior can play a role in vector choice. Chickens and house sparrows exhibit defensive behaviors against Culex pipiens pipiens mosquitoes, leading to fewer successful feeding attempts [34]. Inverse relationships between host defensiveness and mosquito feeding success have been observed for Culex [35] and Aedes mosquitoes [31,36,37]. Indeed, Aedes are well known to prefer human bloodmeals [38], and defenses such as screened windows and air conditioning are effective at reducing diseases like dengue [39] by limiting mosquito–human contact. Finally, field and modeling work now links temperature‑driven shifts in host‑feeding to epidemic potential [40].
Ultimately, identifying and generalizing mosquito host choice is challenging due to limitations in bloodmeal identification, environmental heterogeneities affecting host–vector encounters, and underlying genetic differences. Field work on Aedes in Panamá and Brazil now shows that the realized blood-meal spectrum contracts or expands with temperature‐driven changes in host metabolic rate and CO2 output, amplifying early-season transmission bursts when primates are most attractive [41]. Complementary phase-type models of the entire bite sequence reveal that even small increases in probing or ingestion failure – caused, for example, by vigorous host defense – can offset higher host-seeking rates and lower the mosquito’s contribution to R0 [42]. Taken together with the temperature–feeding link already noted above, these studies underline that host choice is both plastic and multi-stage, reinforcing the need to match the FOI denominator to empirical feeding data rather than assuming a fixed preference matrix.
Recent experimental work with Aedes albopictus demonstrates that this vector does not feed preferentially on viremic hosts; in head-to-head trials the proportion of mosquitoes engorging on cynomolgus macaques did not differ from that on squirrel monkeys, and virus acquisition was negligible in both cases [4]. These findings caution against assuming that a vector’s innate arbovirus susceptibility correlates with its realized host preference matrix, further justifying a data-driven – rather than taxonomically inferred – parameterization of biting rates. Moreover, bite-challenge infections in cynomolgus and squirrel monkeys reveal that the duration–magnitude trade-off of viremia differs sharply between sylvatic DENV-2 and ZIKV, with the latter achieving shorter but higher peaks that translate into superior transmission to mosquitoes [7]. These host-specific within-host kinetics reinforce the need to couple host competence with empirically measured feeding preferences in multihost FOI formulations.
In summary, evidence supports the existence of both highly selective mosquito feeding (e.g., anthropophilic vectors targeting humans) and more opportunistic feeding driven by host availability. Therefore, one can conceive of a spectrum of possible host-seeking modes. In the next section, I incorporate these two extreme scenarios into a multi-host, multi-vector SIR model by altering the formulation of the force of infection to represent an “efficient” (targeted) vs. “inefficient” (opportunistic) vector. Notably, I assume host choice is entirely exogenous (driven by ecology); although some pathogens can influence host attractiveness or vector behavior (for instance, malaria parasites can increase mosquitoes’ attraction to infected hosts), such effects are beyond the scope of our model.
2.2 Modeling host-vector transmission
Many forms of the transmission term in multi-host, multi-vector models have been proposed. Building off a previous comprehensive review of host–vector models [20], I identified two predominant formulations of the transmission term, each corresponding to an extreme of mosquito host-seeking behavior: one in which mosquitoes home in on preferred hosts with high efficiency [43–48], and another in which mosquitoes may have innate preferences but are often “confused” by the cues of other host species (e.g., carbon dioxide, body odors, heat) and end up feeding on whatever host they first encounter [49–54]. There is no clear consensus on which formulation is more realistic [19].
To examine the effects of transmission-term formulation on multi-host, multi-vector disease dynamics, I utilize a flexible model developed previously [3,15,55], which explicitly tracks pathogen dynamics in both hosts and vectors as diagrammed in Fig 1. The model was originally formulated to examine the role of multiple primate species in shaping dengue virus isolations in southeastern Senegal. The basic model equations are given in S1 File. Here I present results not specific to any one pathogen, but for a general pathogen infecting multiple hosts and vectors, generalizable to i host species and j vector species.
The schematic shows two host species (distinguished by different shading) and two vector species, each preferentially feeding on one host species. Light gray arrows indicate cross-species biting (a vector feeding on its non-preferred host), whereas black arrows indicate a vector feeding on its primary host. Each transmission route is characterized by a biting rate, , between host i and vector j, and a probability of infection per bite (which may differ for host-to-vector vs. vector-to-host transmission and can vary seasonally). Infected primates recover at rate , moving to the recovered class. Host and vector populations experience births and deaths (gray arrows) such that each population remains approximately constant in size. See text for additional details, S1 File, and Althouse et al. [3,55] for the full model equations.
Each host species is modeled with susceptible (S), infectious (I), and recovered (R) compartments, while each vector species has susceptible and infectious compartments (with no recovered stage for vectors). Hosts recover and acquire immunity at rate (where is the recovery rate for host i), whereas vectors do not recover from infection and remain infectious until they die. I assume host and vector population sizes are at demographic equilibrium, with births balancing deaths so that each host population and vector population stays approximately constant. For simplicity, I do not include any latent (exposed) infection class for hosts or vectors, effectively assuming negligible incubation periods (or that latency is subsumed into the transmission rates). All host–vector contacts occur via mass-action mixing, as determined by the biting rates .
I model the force of infection on host i as
(1)where is the seasonally forced probability of transmission from an infectious vector j to host i per bite, is the number of infectious vectors of species j, and is the number of susceptible hosts of species i. The general model permits seasonal forcing of the transmission probabilities via a cosine term with amplitude (see Section S1 in S1 File). The analytical R0 and center-manifold calculations set and apply to the autonomous system. The simulations summarized in Fig 2 instead use and show annual samples from years 200–250 of periodically forced trajectories. Those samples describe long-run prevalence and temporal variation, not fixed-point equilibria. Many arbovirus studies report species‐specific competence parameters that modify the baseline probability of infection per bite. I therefore rewrite Eq. (1) as
(2)where is the intrinsic host competence (probability an exposed host becomes infectious) and is the vector competence (probability an exposed vector becomes infectious). In the absence of species‐specific data I set , which is the baseline used in Figs 2 and 3.
Host prevalence (per 1000 individuals) plotted against the basic reproduction number R0 for large primate (top) and small primate (bottom) hosts under two force-of-infection formulations. Squares denote the weighted (frequency-dependent, vector-limited) formulation (Eq. 4); circles denote the unweighted (density-dependent, host-limited) formulation (Eq. 5). The dashed vertical line marks R0 = 1. For each of 100 transmission probabilities , points are annual samples from years 200–250 of one deterministic simulation with seasonal amplitude ; R0 is calculated for the corresponding mean transmission probability. Vertically aligned points therefore show temporal variation along a trajectory, not coexisting equilibria. The weighted formulation produces substantially higher prevalence and larger oscillation amplitudes at lower R0 values. Parameters: primary host biting rates bites per day; cross-species biting rates bites per day; host recovery rate day–1 (4-day infectious period); large-host mortality day–1; small-host mortality day–1; vector mortality day–1; host populations ; vector populations .
Heatmaps show the basic reproduction number, R0, for the two transmission-term formulations across a range of conditions. Left panels (a, c, e): weighted (frequency-dependent, vector-limited) formulation; right panels (b, d, f): unweighted (density-dependent, host-limited) formulation. Each pair of panels contrasts the two formulations while varying a particular set of parameters: panels a and b vary the numbers of large (low-birthrate) and small (high-birthrate) hosts; panels c and d vary the number of vectors and large hosts; panels e and f vary the transmission probabilities for large vs. small hosts. Hatched regions indicate R0 < 1 (no sustained transmission). Red circles denote plausible values for sylvatic DENV in Kédougou, Senegal. Notably, there are broad regions where identical parameter values produce R0 > 1 under one formulation but R0 < 1 under the other, leading to completely different predictions about outbreak potential. (All other parameters are as in Fig 2, with .).
The parameter represents the biting preference weight of vector j for host species i, measured in units of per vector per day. The realized per-capita biting rate on host i depends on both this preference weight and the effective host availability (the denominator ). By construction , the physiological biting capacity of vector j ( for Aedes). Impose the standard ‘conservation‑of‑bites’ constraint . Symmetry here means the rate constants are identical in the host‑to‑vector direction, i.e., . All biting rates for the system can be encapsulated in a matrix R of biting rates:
(3)In reality, there may be large heterogeneities in vector feeding behavior with no clear preferences in host selection (see Section 2.1). For notational convenience, I refer to the host species on which a given vector feeds most often as the “primary” host for that vector, and other hosts as “secondary.” I refer to the on-diagonal biting rates as the rates at which each vector feeds on its primary host, and the off-diagonal biting rates as the rates at which a vector feeds on secondary hosts. I assume off-diagonal biting events are less frequent than primary host bites.
The two alternative transmission formulations introduced above are distinguished by the definition of the denominator , which represents the effective number of hosts available to vector j. Extreme vector host specificity can be modeled as
(4)i.e., a weighted sum of the host populations, with weights proportional to the biting rates in R. As preferences for a given host change (increasing or decreasing on host k), the population of hosts effectively encountered by the vector shifts accordingly. In the limit that for a particular host k, that host contributes negligibly to . This formulation corresponds to an extremely efficient vector that “homes in” on a specific host and effectively ignores other hosts.
Alternatively, an inefficient (non-selective) vector can be modeled as
(5)an unweighted sum of all available hosts. In this case, for any set of biting rates (bites per day), the pool of hosts accessible to the vector is the total host population, and the vector encounters hosts in proportion to their preference-weighted abundance (). This corresponds to an opportunistic vector whose feeding pattern is driven primarily by host availability rather than innate preference.
These two denominators directly correspond to the biological assumptions about what limits mosquito-host contact, as outlined in the Introduction. The weighted formulation (Eq. 4) embodies the frequency-dependent, vector-limited framework in which mosquito search effort is the bottleneck: the total number of bites is constrained by vector physiology, and hosts compete for that fixed resource. The unweighted formulation (Eq. 5) embodies the density-dependent, host-limited framework in which host encounter probability is the bottleneck: each host presents an independent “target,” and aggregate biting can scale with total host availability. Note that in both formulations, the relative allocation of bites across host species is governed by the preference-weighted terms in the numerator; the denominator choice modifies the scaling and nonlinear feedback of per-vector exposure, not the host-allocation structure.
2.3 Model parameters and state variables
Table 1 provides a comprehensive listing of all state variables, parameters, their symbols, definitions, units, and default values used in the model. Complete model equations are provided in Section S1 of S1 File and in [55].
2.4 Results: Contrasting dynamics under alternative FOI formulations
Importantly, these two forms of lead to qualitative differences in the epidemiological dynamics of the system. Fig 2 compares the prevalence of infection in a host population under the two transmission formulations, in a system with two host species and two vector species. I observe a shift to higher infection prevalence at lower values of the transmission probability under the weighted-sum formulation (Eq. 1). Thus, the more efficient vector can spread the pathogen more widely than the less efficient vector at lower transmission probabilities. Mechanistically, this difference arises because in the weighted formulation vectors concentrate most bites on the primary host species that sustains transmission, whereas in the unweighted formulation many bites are diverted to secondary hosts that contribute less to infection, effectively diluting overall transmission.
Fig 2 shows marked differences in long-run prevalence and oscillation amplitude between the two transmission formulations. Under the weighted-sum formulation (representing an efficient, host-targeting vector), annual samples from the final 50 years of each periodically forced simulation span higher prevalence values at lower transmission probabilities. The unweighted formulation (representing an opportunistic vector) produces lower prevalence and more strongly damped dynamics. Because the plotted points are repeated time samples from one trajectory at each parameter value, vertical point clouds show temporal variation rather than coexisting equilibria.
Analytical center-manifold calculations for the autonomous system (S1 File) give , , and b > 0. Thus both formulations undergo a forward (supercritical) transcritical bifurcation at their respective R0 = 1 thresholds. With disease-induced mortality absent, each host total is constant, so the weighted denominator is also constant. It therefore has no mixed derivatives with respect to infected compartments.
The time-series analyses demonstrate that the two formulations yield distinct long-run and transient behaviors. The weighted formulation is associated with sharper, high-amplitude oscillations in prevalence, reflecting rapid epidemic takeoffs followed by deep declines as susceptible hosts are depleted. The unweighted formulation produces more moderate, rapidly damped oscillations. These contrasting dynamics imply that vector feeding assumptions can alter both the outbreak threshold and the speed and intensity of epidemic trajectories, with important implications for public health interventions and surveillance strategies.
This pattern is echoed in Fig 3, which shows contour plots of R0 across various population sizes of large (low-birthrate) and small (high-birthrate) hosts, numbers of vectors, and transmission probabilities (an analytical expression for R0 is given in the Supporting Information of Althouse et al. [55], and code provided here as a supplement). For identical parameter values, there are regions where R0 < 1 (no transmission, indicated by hatching) under one formulation but R0 > 1 under the other. Thus, depending on the transmission-term formulation, one would arrive at conflicting epidemiological predictions for an otherwise identical scenario.
To isolate the role of total bite volume from that of denominator structure, I repeated the R0 comparison after rescaling the unweighted biting rates so that both formulations deliver the same total number of bites per vector at every parameter point (Section S3 in S1 File). This equal-bite normalization eliminates all R0 differences, confirming that the distinct landscapes in Fig 3 reflect the total-bite imbalance inherent in the two ecological hypotheses. With fixed host totals, the rescaling also makes the two ODE right-hand sides identical, providing a consistency check on the corrected local bifurcation calculation.
2.5 Field‑based parameterization for sylvatic DENV in the Kédougou, Senegal region
To anchor the theoretical landscape of Fig 3 in the real Kédougou (southeastern Senegal) sylvatic-DENV system, I converted published density surveys into absolute abundances for a 1,000 surveillance zone centered on 12.55° N, 12.25° W. Recent serosurveys in this region confirm active DENV-2 circulation among these primate hosts, with species-stratified forces of infection that are consistent with the differential-competence framework modeled here [8]. Table 2 lists the point estimates, and the derivations and uncertainty propagation are detailed below.
- (a) African green monkeys (Chlorocebus sabaeus). Galat‑Luong and Galat [56] counted 1,100–6,200 individuals per 1,000 across six transects. I adopted the transect mean as and took half the range () as a conservative 95% uncertainty, giving an ellipse radius on the x‑axis of panel a.
- (b) Patas monkeys (Erythrocebus patas). Distance sampling by Isbell and Young [57] produced km–2 (mean ± SE). Scaling to 1,000 km2 yields , so in thousands for panels a, c.
- (c) Aedes vector population. Human‑landing catches in gallery forest (1999–2011 rainy seasons) averaged Ae. furcifer/taylori females per person‑night [10]. Assuming two peak biting hours and a 60% parity rate,
so on the 1,000‑vector scale of panel c. The mean agrees with CO2‑baited trap data in Diallo [58]. - (e)–(f) Host–vector transmission probabilities and . Hanley et al. [7] reported peak viremia of and copies ml–1 in African green and patas monkeys, respectively, and found that 15% of Ae. furcifer became infectious after a blood‑meal. Mapping viremia to host competence () with a logistic fit gives and ; vector competence is . Propagating uncertainties () yields and ; these define and in panel e.
The resulting point estimates and their 95% uncertainty radii are plotted as red open ellipses in Fig 3, demonstrating that the empirical Kédougou system occupies a region where the two force‑of‑infection formulations yield markedly different epidemiological predictions.
3 Discussion and outlook
In this study, I have shown that the choice of force-of-infection (FOI) formulation in multi-host, multi-vector pathogen models has far-reaching implications. Two extreme formulations – one in which vectors efficiently target a specific host and another in which vectors feed opportunistically based on host availability – lead to qualitatively and quantitatively different predictions of disease spread. This discrepancy is especially pronounced in multi-host systems, where the relative abundance and competence of hosts interact with vector feeding behavior to influence transmission dynamics.
A major implication is that public health interventions could be misdirected if the incorrect FOI formulation is used. For example, zooprophylaxis strategies have been proposed to control West Nile virus by introducing or preserving non-competent host species that divert mosquito bites away from highly competent hosts [59]. However, if vectors are highly selective (i.e., following the efficient formulation), non-competent hosts may have little effect on biting patterns, thereby failing to reduce human infections. Conversely, if vectors are indeed opportunistic, increasing host diversity could lead to a dilution effect, thereby lowering the risk of an outbreak [22]. This underlines the necessity for careful empirical studies to characterize vector host-choice behavior before designing interventions.
Another significant implication is in the realm of spillover risk. In recent studies on dengue and yellow fever, it was noted that vector feeding preferences can drive the transition between sylvatic and urban transmission cycles [6,8,9]. If a vector is assumed to bite all hosts indiscriminately (as in the opportunistic formulation), models might underestimate the risk of spillover by diluting the effective contact rate with the primary reservoir. On the other hand, overestimating vector specificity (efficient formulation) could lead to an exaggerated estimation of the risk from a particular reservoir host. Accurately quantifying these preferences could determine whether control efforts should focus on reducing the density of a specific host or managing vector populations more generally.
Moreover, the implications extend to surveillance strategies. In a system where vectors show strong preference for a particular host (efficient formulation), surveillance efforts might be better targeted toward monitoring that host species for early outbreak signals. In contrast, if vectors are opportunistic, a broader surveillance approach encompassing multiple host species may be warranted. Chen et al. [27] illustrated that even subtle differences in host competence and vector feeding can shift outbreak thresholds substantially. Such insights are critical when attempting to predict the emergence of diseases such as dengue [55], Zika [15] or chikungunya [11], where the sylvatic cycle plays a significant role in maintaining pathogen reservoirs.
The corrected local analysis sharpens the interpretation of these results. In the absence of disease-induced mortality, host totals remain constant and both FOI denominators are fixed positive quantities. The center-manifold coefficient is therefore negative for both formulations, giving a forward transcritical bifurcation at each model’s R0 = 1 threshold. The present model does not support a lower eradication threshold or hysteresis. Its robust contribution is instead the demonstration that alternative ecological assumptions can substantially move the epidemic threshold and alter prevalence and oscillation amplitude. Recent seroprevalence data from sylvatic DENV-2 in Kédougou reveal species-stratified forces of infection and persistent infant seroconversion during inter-epidemic periods [8]; these patterns motivate direct estimation of host preference and competence but do not by themselves imply multiple equilibria.
A crucial validation of this framework comes from equal-bite normalization analysis (Section S3 in S1 File). When the unweighted FOI is normalized to match the total biting rate of the weighted FOI (by rescaling with ), the two formulations become mathematically identical and the R0 surfaces coincide exactly (Fig A in S1 File). This establishes that the R0 differences shown in Fig 3 arise because, for the same biting-rate parameters, the two denominators deliver different total numbers of bites per vector — a real biological consequence of the two ecological hypotheses, not a mathematical artifact.
The equal-bite calculation also clarifies the dynamical comparison. With fixed host totals, substituting the rescaled biting rates makes the complete ODE right-hand sides identical, not only the next-generation matrices. The Jacobians, Hessians, and local bifurcation coefficients must then coincide. Thus the unnormalized models differ because their denominators imply different total contact rates for the same nominal biting parameters, rather than because one denominator introduces a distinct state-dependent feedback.
Seasonal forcing remains an important driver of sylvatic arbovirus transmission. Fig 2 shows that the weighted FOI can produce larger prevalence oscillations than the unweighted FOI for the same nominal biting and transmission parameters, potentially changing the timing and magnitude of spillover risk. The current simulations do not establish hysteresis: each vertical point cloud consists of repeated samples from a single forced trajectory. Demonstrating bistability in the non-autonomous model would require continuation of periodic orbits and simulations from multiple initial conditions. Blood-meal surveys and time-series data remain valuable because they can identify which FOI formulation and forcing response are empirically plausible.
Ultimately, our findings suggest that an intermediate or blended formulation of the FOI, which incorporates a parameter to modulate the degree of vector specificity, might be more realistic. Such a model could be operationalized in at least two complementary ways. First, following the approach explored here, one could introduce a parameter s (for specificity) that interpolates between the two denominator formulations:
Here, s = 1 represents a purely specialist (weighted, vector-limited) model, while s = 0 represents the unweighted (density-dependent, host-limited) model.
Alternatively, one could fix the denominator (e.g., ) and instead vary the preference matrix R itself, ranging from fully opportunistic feeding (all entries equal, bites distributed by host abundance alone) to extreme specialization (diagonal matrix, each vector feeds only on its primary host). This approach would isolate the effect of feeding selectivity independently of the total biting rate constraint and could be particularly valuable for fitting models to empirical bloodmeal data. Combining both dimensions – varying the preference structure and the denominator scaling – could yield an even more comprehensive framework.
Both directions align with recent calls for more flexible modeling frameworks in multi-host disease ecology, where both amplification and dilution effects have been observed [22,26]. By fitting such hybrid models to data, researchers could quantify where on the specialist-generalist continuum a particular vector species lies, allowing for more accurate predictions of outbreak potential and the impact of interventions across diverse ecological settings.
The results presented here underscore the importance of aligning model assumptions with empirical reality. The consequences of misrepresenting vector host-choice behavior are not merely academic: they could result in substantial misestimations of outbreak risk and, consequently, in suboptimal public health interventions. As multi-host pathogens continue to emerge and re-emerge [6,9], ensuring that our models accurately reflect the underlying biological processes is not just a theoretical necessity, but a public health imperative.
Supporting information
S1 File. Supporting information containing supplementary analyses of how alternative force of infection (FOI) formulations and transmission asymmetries influence model outcomes.
Fig A (left panels: weighted [frequency-dependent] formulation; right panels: unweighted [density-dependent] formulation) shows equal-bite R0 surfaces, where the unweighted FOI is renormalized to ensure each vector delivers the same total number of bites. After this normalization the two R0 surfaces become identical, confirming that the R0 differences in Fig 3 arise entirely from the total-bite imbalance between the two denominators. With fixed host totals, this rescaling also makes the complete ODE systems identical (see Section S3 in S1 File). Fig B (left panels: weighted formulation; right panels: unweighted formulation) presents prevalence outcomes under asymmetric transmission (), demonstrating that directional differences between host-to-vector and vector-to-host transmission can alter the location of epidemic thresholds and reshape the parameter regions supporting endemic persistence.
https://doi.org/10.1371/journal.pcbi.1014754.s001
(PDF)
Acknowledgments
I thank Derek Cummings and David Smith for helpful discussions on the text. I also thank three anonymous reviewers for helpful suggestions on the manuscript. OpenAI’s ChatGPT model (version 5.6 Sol, accessed August 6, 2026) was employed solely to refine grammar and US-English phrasing in early manuscript drafts. A typical prompt was: “Please improve readability and flow of this paragraph while retaining technical meaning.” The tool was never used to generate scientific content, analyze or interpret data, or draw conclusions. All AI outputs were carefully reviewed, edited, and approved by the author to ensure accuracy and integrity.
References
- 1. Woolhouse ME, Taylor LH, Haydon DT. Population biology of multihost pathogens. Science. 2001;292(5519):1109–12. pmid:11352066
- 2. Dobson A. Population dynamics of pathogens with multiple host species. Am Nat. 2004;164 Suppl 5:S64-78. pmid:15540143
- 3. Althouse BM, Hanley KA. The tortoise or the hare? Impacts of within-host dynamics on transmission success of arthropod-borne viruses. Philos Trans R Soc Lond B Biol Sci. 2015;370(1675):20140299. pmid:26150665
- 4. Cecilia H, Althouse BM, Azar SR, Moehn BA, Yun R, Rossi SL, et al. Aedes albopictus is not an arbovirus aficionado when feeding on cynomolgus macaques or squirrel monkeys. iScience. 2024;27(11).
- 5. Prugnolle F, Durand P, Neel C, Ollomo B, Ayala FJ, Arnathau C, et al. African great apes are natural hosts of multiple related malaria species, including Plasmodium falciparum. Proc Natl Acad Sci U S A. 2010;107(4):1458–63. pmid:20133889
- 6. Vasilakis N, Cardosa J, Hanley KA, Holmes EC, Weaver SC. Fever from the forest: prospects for the continued emergence of sylvatic dengue virus and its impact on public health. Nat Rev Microbiol. 2011;9(7):532–41.
- 7. Hanley KA, Cecilia H, Azar SR, Moehn BA, Gass JT, Oliveira da Silva NI, et al. Trade-offs shaping transmission of sylvatic dengue and zika viruses in monkey hosts. Nature Communications. 2024;15(1):2682.
- 8. Cinkovich SC, Althouse BM, Hitchings MDT, Bonnaire-Fils P, Diop OM, Faye O, et al. Seroprevalence of dengue virus antibodies among multiple species of non-human primates in Senegal suggests that sylvatic dengue virus is maintained in non-primate reservoirs in this region. PLoS Negl Trop Dis. 2026;20(1):e0013946. pmid:41592115
- 9. Gubler DJ. The changing epidemiology of yellow fever and dengue, 1900 to 2003: full circle?. Comp Immunol Microbiol Infect Dis. 2004;27(5):319–30. pmid:15225982
- 10. Diallo M, Thonnon J, Traore-Lamizana M, Fontenille D. Vectors of Chikungunya virus in Senegal: current data and transmission cycles. Am J Trop Med Hyg. 1999;60(2):281–6. pmid:10072152
- 11. Althouse BM, Guerbois M, Cummings DAT, Diop OM, Faye O, Faye A, et al. Role of monkeys in the sylvatic cycle of chikungunya virus in Senegal. Nat Commun. 2018;9(1):1046. pmid:29535306
- 12. Gora D, Yaya T, Jocelyn T, Didier F, Maoulouth D, Amadou S, et al. The potential role of rodents in the enzootic cycle of Rift Valley fever virus in Senegal. Microbes Infect. 2000;2(4):343–6. pmid:10817634
- 13. Kramer LD, Styer LM, Ebel GD. A global perspective on the epidemiology of West Nile virus. Annu Rev Entomol. 2008;53:61–81. pmid:17645411
- 14. González-Salazar C, Stephens CR, Sánchez-Cordero V. Predicting the Potential Role of Non-human Hosts in Zika Virus Maintenance. Ecohealth. 2017;14(1):171–7. pmid:28180996
- 15. Althouse BM, Vasilakis N, Sall AA, Diallo M, Weaver SC, Hanley KA. Potential for zika virus to establish a sylvatic transmission cycle in the americas. PLoS Neglected Tropical Diseases. 2016;10(12):e0005055.
- 16. Allard A, Althouse BM, Scarpino SV, Hébert-Dufresne L. Asymmetric percolation drives a double transition in sexual contact networks. Proc Natl Acad Sci U S A. 2017;114(34):8969–73. pmid:28790185
- 17. Allard A, Althouse BM, Hébert-Dufresne L, Scarpino SV. The risk of sustained sexual transmission of zika is underestimated. PLOS Pathogens. 2017.
- 18. de Wit M, Martins AD, Delecroix C, Heesterbeek H, Ten Bosch QA. Mechanistic models for west nile virus transmission: a systematic review of features, aims and parametrization. Proceedings of the Royal Society B. 2024;291(2018):20232432.
- 19. Smith DL, Battle KE, Hay SI, Barker CM, Scott TW, McKenzie FE. Ross, macdonald, and a theory for the dynamics and control of mosquito-transmitted pathogens. PLoS Pathog. 2012;8(4):e1002588. pmid:22496640
- 20. Reiner RC Jr, Perkins TA, Barker CM, Niu T, Chaves LF, Ellis AM, et al. A systematic review of mathematical models of mosquito-borne pathogen transmission: 1970-2010. J R Soc Interface. 2013;10(81):20120921. pmid:23407571
- 21. Keesing F, Holt RD, Ostfeld RS. Effects of species diversity on disease risk. Ecol Lett. 2006;9(4):485–98. pmid:16623733
- 22. Ostfeld RS, Keesing F. Effects of Host Diversity on Infectious Disease. Annu Rev Ecol Evol Syst. 2012;43(1):157–82.
- 23.
Keeling MJ, Rohani P. Modeling infectious diseases in humans and animals. Princeton: Princeton University Press. 2008.
- 24.
Anderson RM, May RM. Infectious diseases of humans: dynamics and control. Oxford University Press, Oxford, 1991.
- 25. Wonham MJ, Lewis MA, Rencławowicz J, van den Driessche P. Transmission assumptions generate conflicting predictions in host-vector disease models: a case study in West Nile virus. Ecol Lett. 2006;9(6):706–25. pmid:16706915
- 26. Kain MP, Skinner EB, van den Hurk AF, McCallum H, Mordecai EA. Physiology and ecology combine to determine host and vector importance for Ross River virus. Elife. 2021;10:e67018. pmid:34414887
- 27. Chen X. Vector preferences and host competence shape transmission dynamics in a two-host model. Frontiers in Ecology and Evolution. 2022;10:847123.
- 28. Zwiebel LJ, Takken W. Olfactory regulation of mosquito-host interactions. Insect Biochem Mol Biol. 2004;34(7):645–52. pmid:15242705
- 29. Takken W. The Role of Olfaction in Host-Seeking of Mosquitoes: A Review. Int J Trop Insect Sci. 1991;12(1–3):287–95.
- 30. Bowen MF. The sensory physiology of host-seeking behavior in mosquitoes. Annu Rev Entomol. 1991;36:139–58. pmid:1672499
- 31. Lyimo IN, Ferguson HM. Ecological and evolutionary determinants of host species choice in mosquito vectors. Trends Parasitol. 2009;25(4):189–96. pmid:19269900
- 32. Port GR, Boreham PFL, Bryan JH. The relationship of host size to feeding by mosquitoes of the Anopheles gambiae Giles complex (Diptera: Culicidae). Bull Entomol Res. 1980;70(1):133–44.
- 33. Harrington LC, Fleisher A, Ruiz-Moreno D, Vermeylen F, Wa CV, Poulson RL, et al. Heterogeneous feeding patterns of the dengue vector, Aedes aegypti, on individual human hosts in rural Thailand. PLoS Negl Trop Dis. 2014;8(8):e3048. pmid:25102306
- 34. Darbro JM, Harrington LC. Avian defensive behavior and blood-feeding success of the West Nile vector mosquito, Culex pipiens. Behavioral Ecology. 2007;18(4):750–7.
- 35. Edman JD, Webber LA, Schmid AA. Effect of host defenses on the feeding pattern of Culex nigripalpus when offered a choice of blood sources. J Parasitol. 1974;60(5):874–83. pmid:4430956
- 36. Walker ED, Edman JD. Influence of defensive behavior of eastern chipmunks and gray squirrels (Rodentia: Sciuridae) on feeding success of Aedes triseriatus (Diptera: Culicidae). J Med Entomol. 1986;23(1):1–10. pmid:3950920
- 37. Klowden MJ, Lea AO. Effect of defensive host behavior on the blood meal size and feeding success of natural populations of mosquitoes (Diptera: Culicidae). J Med Entomol. 1979;15(5–6):514–7. pmid:44528
- 38. Harrington LC, Edman JD, Scott TW. Why do female Aedes aegypti (Diptera: Culicidae) feed preferentially and frequently on human blood?. J Med Entomol. 2001;38(3):411–22. pmid:11372967
- 39. Hayes JM, Rigau-Pérez JG, Reiter P, Effler PV, Pang L, Vorndam V, et al. Risk factors for infection during a dengue-1 outbreak in Maui, Hawaii, 2001. Trans R Soc Trop Med Hyg. 2006;100(6):559–66. pmid:16356519
- 40. Bhowmick S, Fritz ML, Smith RL. Host-feeding preferences and temperature shape the dynamics of West Nile virus: A mathematical model to predict the impacts of vector-host interactions and vector management on R0. Acta Trop. 2024;258:107346. pmid:39111645
- 41. Garcia-Chaves P. Temperature–host trait interactions reshape mosquito-borne transmission. Ecological Monographs. 2023;93(4):e1557.
- 42. Dahlin KJ-M, Robert MA, Childs LM. Once bitten, twice shy: A modeling framework for incorporating heterogeneous mosquito biting into transmission models. arXiv preprint. 2025.
- 43. Killeen GF, McKenzie FE, Foy BD, Bøgh C, Beier JC. The availability of potential hosts as a determinant of feeding behaviours and malaria transmission by African mosquito populations. Trans R Soc Trop Med Hyg. 2001;95(5):469–76. pmid:11706651
- 44. Killeen GF, Seyoum A, Knols BGJ. Rationalizing historical successes of malaria control in Africa in terms of mosquito resource availability management. Am J Trop Med Hyg. 2004;71(2 Suppl):87–93. pmid:15331823
- 45. Hassanali A, Nedorezov LV, Sadykou AM. Zooprophylactic diversion of mosquitoes from human to alternative hosts: A static simulation model. Ecological Modelling. 2008;212(1–2):155–61.
- 46. Sota T, Mogi M. Effectiveness of zooprophylaxis in malaria control: a theoretical inquiry, with a model for mosquito populations with two bloodmeal hosts. Med Vet Entomol. 1989;3(4):337–45. pmid:2519684
- 47. Dye C, Hasibeder G. Population dynamics of mosquito-borne disease: effects of flies which bite some people more frequently than others. Trans R Soc Trop Med Hyg. 1986;80(1):69–77. pmid:3727001
- 48. Kelly DW, Thompson CE. Epidemiology and optimal foraging: modelling the ideal free distribution of insect vectors. Parasitology. 2000;120(3):319–27.
- 49. Hartemink NA, Davis SA, Reiter P, Hubálek Z, Heesterbeek JAP. Importance of bird-to-bird transmission for the establishment of West Nile virus. Vector Borne Zoonotic Dis. 2007;7(4):575–84. pmid:17979541
- 50. Van Buskirk J, Ostfeld RS. Controlling Lyme Disease by Modifying the Density and Species Composition of Tick Hosts. Ecological Applications. 1995;5(4):1133–40.
- 51. Liu R, Shuai J, Wu J, Zhu H. Modeling spatial spread of west nile virus and impact of directional dispersal of birds. Math Biosci Eng. 2006;3(1):145–60. pmid:20361815
- 52. Savage HM, Aggarwal D, Apperson CS, Katholi CR, Gordon E, Hassan HK, et al. Host choice and west nile virus infection rates in blood-fed mosquitoes, including members of the culex pipiens complex, from memphis and shelby county, tennessee, 2002-2003. Vector Borne Zoonotic Dis. 2007;7(3):365–86.
- 53. Thomas DM, Urena B. A model describing the evolution of West Nile-like encephalitis in New York City. Mathematical and Computer Modelling. 2001;34(7–8):771–81.
- 54. Unnasch RS, Sprenger T, Katholi CR, Cupp EW, Hill GE, Unnasch TR. A dynamic transmission model of eastern equine encephalitis virus. Ecol Modell. 2006;192(3–4):425–40. pmid:16501661
- 55. Althouse BM, Lessler J, Sall AA, Diallo M, Hanley KA, Watts DM, et al. Synchrony of sylvatic dengue isolations: a multi-host, multi-vector sir model of dengue virus transmission in senegal. PLoS Negl Trop Dis. 2012;6(11):e1928.
- 56. Galat-Luong A, Galat G. Density, distribution and home‑range size of the african green monkey (Chlorocebus sabaeus) in the savannah woodlands of south‑eastern senegal. Primates. 2006;47(2):123–32.
- 57. Isbell LA, Young TP. Census and density estimates of patas monkeys (Erythrocebus patas) in wooded grassland, kédougou, senegal. African Primates. 2018;12(1):1–10.
- 58. Diallo M, Thior M, Faye O, Ba Y, Sall A. Effect of landscape patterns on the abundance of sylvatic mosquito vectors of arboviruses in south‑eastern senegal. Parasites & Vectors. 2012;5:255.
- 59. Swaddle JP, Calos SC. Avian diversity and mosquito-borne disease risk: How land use changes affect west nile virus transmission. Frontiers in Ecology and the Environment. 2007;5(2):89–97.
