Formal Model Article Format |
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Corresponding author: Elżbieta Ziółkowska ( e.ziolkowska@uj.edu.pl ) Academic editor: Fabio Sgolastra
© 2026 Elżbieta Ziółkowska, Grzegorz Sowa, Xiaodong Duan, Christopher John Topping.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Ziółkowska E, Sowa G, Duan X, Topping CJ (2026) The Formal Model for the hoverfly Sphaerophoria scripta (Diptera, Syrphidae) agent-based model in the Animal Landscape and Man Simulation System (ALMaSS). Food and Ecological Systems Modelling Journal 7: e169793. https://doi.org/10.3897/fmj.7.169793
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We present a formal model for the aphidophagous hoverfly Sphaerophoria scripta, a species widely used for biological control of Myzus persicae and other aphids, as well as for pollination services. The model is structured for integration within the Animal Landscape and Man Simulation System (ALMaSS) to investigate population dynamics under variable field conditions, with the overarching aim of improving regulatory risk assessments of pesticide impacts on hoverflies. Our approach is individual-based, spatially explicit, and operates on a daily time step. The principal model drivers include temperature, the spatial and temporal distribution of aphid prey for larvae, and the availability of nectar and pollen resources for adult females. Dispersal functions are designed to interact dynamically with foraging and oviposition behaviours, with daily activity patterns governed by the interplay between reproductive objectives and foraging requirements. Key life-history parameters, including egg incubation duration, larval instar development, pupariation, adult longevity, and fecundity, were derived from available laboratory and field studies. The prototype model defines state transitions, developmental thresholds, mortality functions, and foraging-oviposition behaviours, and is prepared for calibration and scenario-based application.
Agroecosystem, aphidophagous hoverfly, biological control, Long Hoverfly, pollinator, population dynamics, spatially-explicit model
Growing recognition of wild pollinators has highlighted their crucial role in sustainable agriculture and ecosystem functioning. While most research and conservation efforts have historically focused on managed species such as the honey bee, wild pollinators contribute significantly to pollination services and offer additional ecosystem benefits (
Hoverflies (Diptera, Syrphidae), also known as syrphids or flower flies, are globally distributed and are among the most important insect pollinators (
Given this dual ecological role, pollination by adults and pest control by larvae, we selected Sphaerophoria scripta (Linnaeus, 1758) as a focal species for model development. Sphaerophoria scripta is one of the most common aphidophagous hoverflies in Central Europe (
This paper follows the formal model structure outlined by
Several individual-based models have been developed so far to simulate hoverfly population dynamics, particularly focusing on aphidophagous species. RePast hoverfly-aphid model (
In contrast, movement and foraging are modelled more realistically, incorporating non-random prey search, oviposition optimisation, and larval predation using an exponential function dependent on hoverfly age and aphid density. Interactions between adult hoverflies and the landscape are not explicitly modelled, aside from oviposition behaviour and larval predation. Notably, pollination by adults and its influence on movement and oviposition are not included.
Two other individual-based models focus specifically on Episyrphus balteatus (De Geer, 1776). The ‘Hover-Winter’ model (
The SyrFitSources model (
Building on concepts from the models described above, our model of S. scripta introduces increased realism, particularly in landscape representation. It will be integrated into the highly detailed, dynamic landscape simulation available in ALMaSS, which operates at a spatial resolution of 1 m2 (
To complement the S. scripta model and capture the broader functional diversity of hoverflies, a second model is under development for the species Eristalis tenax (Linnaeus, 1758), whose larvae are saprophagous (
The model provides a spatially explicit, mechanistic representation of S. scripta population dynamics in temperate agricultural landscapes, with individual development and survival rates driven by ambient temperature and aphid prey density. Its primary purpose is to evaluate hoverfly efficacy and resilience under alternative climate and crop-management scenarios. A secondary application is to model a representative non-target species within a systems-based environmental risk-assessment framework for agrochemicals, particularly pesticides.
We will implement the model in the ALMaSS framework (
The model aims to represent the development, survival, movement, foraging, and reproduction of S. scripta using an individual-based approach within the ALMaSS framework. This approach enables a mechanistic simulation of hoverfly population dynamics in response to key ecological drivers, particularly temperature and prey density, with a level of detail suitable for long-term ecological projections and agricultural management scenarios.
As with other published models in ALMaSS (
The ALMaSS environment provides a detailed, spatially and temporally dynamic representation of agricultural landscapes. This environment includes a raster-based land-cover map at 1 m2 resolution, overlaid with polygonal habitat data. Landscapes are composed of individual farm units that are grouped and classified by type (e.g. arable, grassland, non-crop, mixed, or livestock farms), and each farm is governed by tailored crop management regimes. These regimes define the timing and probability of farm activities, including pesticide application and are structured as pluri-annual crop rotations based on real agronomic practices.
Daily updates to landscape conditions include vegetation growth and weather, both of which affect resource availability. The aphid population dynamics could be explicitly simulated (i.e., the model could be linked with the aphid subpopulation model of
All life stages of S. scripta—egg, larva, pupa, and adult—are modelled individually. Parameters are based on the field and laboratory data on S. scripta or similar species within the genus if available in the literature. Interactions with the landscape and other individuals are updated daily, enabling realistic simulation of individual and population-level dynamics within complex agricultural mosaics.
The life cycle of this highly migratory syrphid comprises four principal stages, egg, larva, pupa and adult. It unfolds over multiple generations between April and November (and potentially year-round in southern Europe). Overwintering occurs predominantly at the fully grown larval stage, with individuals remaining inactive in the soil or leaf litter. Following spring warming, larvae resume development, pupate, and subsequently emerge as adults. Newly emerged adults disperse into open habitats and engage in low, erratic flight among grasses while visiting a broad spectrum of flowers (
Gravid females locate aphid-infested host plants, ranging from wild herbaceous species to economically important crops such as Avena, Brassica, Cichorium, Lactuca, Triticum and Vicia, as well as apple orchards, on which they oviposit (
Fully grown larvae then harden to create a puparium. This pupal phase endures for approximately one week, during which metamorphosis to the adult form occurs (
Geographical variation in degree‐day requirements shows that mean thermal sums for insect egg development increase from tropical to temperate populations, reflecting local adaptation to cooler climates (
During the egg stage, S. scripta exhibits a clear inverse relationship between temperature and developmental duration (Table
Summary of thermally induced length of development of subsequent life stages for genus of Sphaerophoria.
| Life stage | Temperature (°C) | Relative humidity (%) | Type of food | Food availability | Duration (days) | Conditions /Notes | Species | Reference |
|---|---|---|---|---|---|---|---|---|
| Egg | ≈ 20 | 3–4 | Laboratory temp. | Sphaerophoria scripta | ||||
| 10 | 60–70 | 12 | Sphaerophoria scripta | |||||
| 15 | 6 | |||||||
| 20 | 4 | |||||||
| 25 | 3 | |||||||
| 30 | ~2.3 | |||||||
| 20–22 | 3–4 | |||||||
| 14–17 | 5–6 | Sphaerophoria scripta | ||||||
| 22–32 | 2–3 | Laboratory temp. Very wide temp range and no details on temp regime in the lab. | Sphaerophoria scripta | |||||
| 20 | 50 | 5.50 | Sphaerophoria rueppellii | |||||
| 20 | 90 | 3.55 | ||||||
| 25 | 50 | 4.72 | ||||||
| 25 | 90 | 2.93 | ||||||
| 30 | 50 | 3.89 | ||||||
| 30 | 90 | 2.36 | ||||||
| 20 | 6–12 | Laboratory temp. | Sphaerophoria cylindrica | |||||
| 19.33 | 4.39 | Sphaerophoria sulphuripes | ||||||
| 27.9 ± 1.1 | 1.96 ± 0.07 | Allograpta (Sphaerophoria) javana | ||||||
| 16–18 | 80 | 6–8 | Sphaerophoria scripta | |||||
| 18–20 | 70 | 4–6 | ||||||
| Larva | ≈ 20 | Myzus persicae | Ad libitum | 8 | 50% population Laboratory temp. | Sphaerophoria scripta | ||
| 21 | 80 | Aphis fabae | Ad libitum | 11 | Sphaerophoria scripta | |||
| 27.1 | 77.3 | Hyalopterus pruni | Ad libitum | 3.19 ± 0.22 | First instar | Sphaerophoria scripta | ||
| 3.86 ± 0.23 | Second instar | |||||||
| 6.95 ± 0.38 | Third instar | |||||||
| 14.00 ± 0.34 | Total | |||||||
| 20–22 | unknown | unknown | 4.1 ± 1.0 | Third instar | Sphaerophoria scripta | |||
| ≈ 20 | Acyrthosiphon pisum | unknown | 9 | Near natural temp. | Sphaerophoria scripta | |||
| ≈ 20 | Acyrthosiphon pisum | 5 larvae/day | 14 | Near natural temp. | Sphaerophoria scripta | |||
| 10 larvae/day | 15 | |||||||
| 15 larvae/day | 13 | |||||||
| Larva | 20 larvae/day | 13 | ||||||
| 30 larvae/day | 13 | |||||||
| 40 larvae/day | 12 | |||||||
| 60 larvae/day | 10 | |||||||
| 14–17 | Ad libitum | 13–15 | Sphaerophoria scripta | |||||
| 22–24 | Ad libitum | 12–15 | Sphaerophoria scripta | |||||
| 22 | Ad libitum | 9 | Sphaerophoria scripta | Laska (1959) | ||||
| 22–32 | Ad libitum | 9–14 | Laboratory temp. Very wide temp range and no details on temp regime in the lab. | Sphaerophoria scripta | ||||
| 20 | 90 | Myzus persicae | Ad libitum | 10.95 | Sphaerophoria rueppellii | |||
| 25 | 90 | 8.92 | ||||||
| 30 | 90 | 8.14 | ||||||
| 20 | 8.22 | High food availability | ||||||
| 10.42 | Low food availability | |||||||
| ≈ 20 | 16–27 | Laboratory temp. | Sphaerophoria cylindrica | |||||
| 19.33 | 13.50 | Sphaerophoria sulphuripes | ||||||
| 27.9 ± 1.1 | 2.07 ± 0.11 | First instar | Allograpta (Sphaerophoria) javana | |||||
| 2.06 ± 0.15 | Second instar | |||||||
| 2.18 ± 0.10 | Third instar | |||||||
| 6.30 ± 0.22 | Total | |||||||
| Pupa | 15 | 16 | Sphaerophoria scripta | |||||
| 20 | 10 | |||||||
| 24 | 7.4 ± 0.5 | |||||||
| 25 | 7 | |||||||
| 30 | 6 | |||||||
| 15 | 15.5 | Sphaerophoria scripta | ||||||
| 18 | 11 | |||||||
| 51 | 8.2 | |||||||
| 24 | 7.9 | |||||||
| ≈ 20 | 6–7 | Laboratory temp. | Sphaerophoria scripta | |||||
| ≈ 20 | 6.35 ± 1.5 | Laboratory temp. | Sphaerophoria scripta | |||||
| 21 | 7.8 | Sphaerophoria scripta | Laska (1959) | |||||
| 14–17 | 14–15 | Sphaerophoria scripta | ||||||
| Pupa | 22–32 | 5–7 | Laboratory temp. Very wide temp range and no details on temp regime in the lab. | Sphaerophoria scripta | ||||
| 20 | 50 | 8.79 | Sphaerophoria rueppellii | |||||
| 20 | 90 | 9.14 | ||||||
| 25 | 50 | 5.15 | ||||||
| 25 | 90 | 5.20 | ||||||
| 30 | 50 | 4.90 | ||||||
| 30 | 90 | 4.80 | ||||||
| 20 | 5.66 | High food availability at the larval stage | ||||||
| 5.70 | Low food availability at teh larval stage | |||||||
| ≈ 20 | 5–10 | Laboratory temp. | Sphaerophoria cylindrica | |||||
| 19.33 | 9.77 | Sphaerophoria sulphuripes | ||||||
| 27.9 ± 1.1 | 5.38 ± 0.04 | Allograpta (Sphaerophoria) javana | ||||||
| Egg–adult total | ≈ 20 | 17 ± 3 | Laboratory temp. | Sphaerophoria scripta | ||||
| 14–17 | 32–36 | Sphaerophoria scripta | ||||||
| 19.33 | 27.78 | Sphaerophoria sulphuripes | ||||||
| 27.9 ± 1.1 | 14.02 ± 0.20 | Allograpta (Sphaerophoria) javana |
The larval stage is the longest and most ecologically significant period of syrphid development, as larvae serve as efficient predators of aphids and other soft-bodied insects (
At moderate temperatures (~20 °C), development of S. scripta typically spans 8 to 12 days when food is provided ad libitum (
Prey availability is a critical determinant of aphidophagous hoverfly larval development. At low prey densities, larval development is longer and pupation occurs at lower larval weights (
Equation 1
Equation 2
where Dl is larva developmental time, Na is the number of aphids available daily, and Nc is the number of aphids consumed daily.
Similarly, S. rueppellii larvae reared on M. persicae at 20 °C developed significantly faster under high food availability than under limited prey conditions (8.3 vs. 10.5 days) and pupation occurred at lower larval weights (11 vs. 9.3 mg) (
To date, no published studies have investigated larval longevity under starvation conditions in S. scripta. However,
Larvae of Sphaerophoria species are generalist predators, primarily consuming a variety of aphid species. Larvae of S. scripta have been found feeding on more than 30 genera of aphids. They have also been observed feeding on psyllids (jumping plant lice) and even lepidopteran larvae (e.g., Pieris brassicae), although aphids remain their primary prey (
S. scripta larvae are aphid-feeding on herbaceous plants, including various crop plants, e.g. Avena, Brassica, Cichorium, Lactuca, Triticum, Vicia (
Studies indicate that S. scripta larvae need a daily minimum of five A. pisum aphids for complete development (
Aphid consumption by S. scripta larvae exhibits a pronounced ontogenetic increase, with minimal feeding activity observed during the initial 0–30% of the larval stage. This is followed by a rapid escalation in predation rates between 40 and 70–80% of development, culminating in peak consumption, which then decreases during the final 20–30% prior to pupation (Fig.
Average number of aphids eaten (A) daily and (B) in relation to larval developmental time (expressed as % of time taken from egg hatch to pupation) by syrphid larvae from the Sphaerophoria genus. Based on studies of
Equation 3
where kd is an estimated number of aphids killed per larva per day, MRKR is a mean relative aphid kill rate for the instar, W1 is the weight of the syrphid larva, Wa is a mean aphid weight, and D is the percentage of total larval development achieved in one day at the prevailing temperatures. For E. corollae, MRKR values were 0.29, 0.16, and 0.09 mg × mg-1 × percent-1 for first, second, and third instar, respectively.
Although empirical data on the relationship between larval biomass and aphid predation are not available for S. scripta,
Equation 4
where Ml is fresh larva weight and d is day of development.
They further investigated daily aphid biomass kill by larvae (Ba) in relation to larva fresh weight (Ml) and described it using the linear relationship (Equation 5):
Equation 5
Findings for S. sulphuripes of
Growth of Sphaerophoria sulphuripes larvae (A) and biomass of Nasonovia ribisnigri (Mosley, 1841) killed by S. sulphuripes larvae expressed as mg per 1% of the duration of larval stage (B). Functions were fitted based on data from
Food utilisation in S. scripta is strongly dependent on aphid density. Experimental data from
Parameters of the logistic and Gaussian functions fitted to the data on growth of Sphaerophoria sulphuripes larvae from
| Parameter | Logistic | Gaussian |
|---|---|---|
| a | 14.89 | 14.78 |
| b | 0.0665 | 81.20 |
| c | 41.22 | 33.13 |
| R2 | 0.92 | 0.96 |
Parameters of the Holling Type II response functions fitted to the data on food utilisation from
| Parameter | II instar | III instar | Total larva |
|---|---|---|---|
| a | 1.495 | 1.028 | 0.820 |
| h | 0.031 | 0.021 | 0.036 |
| R2 | 0.92 | 0.96 | 0.95 |
Equation 6
where f denotes the intake rate and R denotes food (or resource) density; a is the attack rate (i.e., the rate at which the hoverfly larva encounters food items per unit of food density), and h is handling time (i.e., the average time spent on processing a food item).
During the pupal stage, syrphid larvae undergo metamorphosis into adults. This transformation is also temperature-dependent. At 15 °C, pupation requires up to 16 days (
The model will consider S. scripta behaviour of all four life stages (i.e., egg, larva with three instars, pupa, and adult) daily. We assume a ratio of 1:1 of females to males at the population level and thus, males will not be included in the model. It is further assumed that all adult females are fertilised; therefore, mating behaviour is not explicitly modelled, although it is implicitly incorporated into the timing of the reproductive process.
The development will be modelled according to the life-stage state machine and transition path (Fig.
Sphaerophoria scripta state diagram showing development from egg to adult female. All stages could transition to state Dying from any other behavioural state due to external messaging. The Overwintering and Migration states (dashed lines) only occurs for the last, autumn generation. It is assumed that a proportion of the population migrates, whereas the remainder reproduces, producing larvae that subsequently enter overwintering. Additionally, a subset of individuals may migrate into the landscape during the subsequent spring.
Larval development occurs on herbaceous vegetation and aphid-infested crops, and is driven by ambient temperature and aphid biomass consumption, which is a function of aphid density. Larvae are capable of moving across plant surfaces in search of prey. This movement is assumed to be density-dependent; in high-density aphid colonies, larvae are likely to remain localised, whereas in low-density conditions, they may actively search for prey. Although precise data on larval mobility are lacking, movement is generally slow and localised, likely limited to several centimetres to tens of centimetres per day, depending on prey availability and plant architecture. First instar larvae are less mobile than later instars and typically remain near the hatching site.
The model assumes that aphid density is provided daily at a spatial resolution of 10 × 10 metres, consistent with the resolution of the ALMaSS aphid subpopulation model (
Larvae eventually pupate, entering a non-mobile stage with temperature-dependent development. Pupae develop into adult females, initiating the next generation. Under favourable conditions, one generation follows another without interruption until autumn. The final generation of the season either migrates or produces larvae that overwinter in a fully developed state. Each ontogenetic stage is associated with a distinct, stage-specific probability of mortality (refer to section ‘Mortality’).
Temperature-dependent development of pre-imaginal stages of S. scripta was modelled using development rates (inverse of development time, day–1). Exploratory analyses indicated that the relationship between temperature and development rate differed among life stages. For egg and pupal stages, the development rate increases monotonically across the observed temperature range, with no evidence of a decline at high temperatures. Consequently, these stages will be modelled using linear degree-day models (Equation 7), expressed as:
Equation 7
where r(T) is the development rate, T is temperature, a is the thermal sensitivity (slope), and T0 is the lower developmental threshold. Linear degree-day models are appropriate when the development rate responds linearly to temperatures above a threshold and when experimental data do not include temperatures near the upper thermal limit. For these stages, the thermal constant (degree-days required to complete development) was calculated as the inverse of the slope parameter (Table
Stage-specific parameter for relationship describing temperature-related development in pre-imaginal stages of Sphaerophoria scripta. Functions fitted based on data in Table
| Developmental stage | Model type | a [day-1×°C] | T0 [°C)] | 95% CI [°C] | K [degree-days] | 95% CI [DD] | Topt [°C] | R2 |
|---|---|---|---|---|---|---|---|---|
| Egg | Degree-day (linear) | 0.0180 | 6.1 | 4.6–8.9 | 55.6 | ~50–65 | – | 0.93 |
| Larva* | Gaussian | – | – | – | – | – | 20.6 | 0.56 |
| Pupa | Degree-day (linear) | 0.0068 | 3.6 | -7.5–8.0 | 146.2 | ~100–250 | – | 0.88 |
In contrast, larval development exhibited a unimodal response to temperature, with a clear maximum at intermediate temperatures and reduced development rates at higher temperatures. Because larval development is strongly influenced by aphid prey availability, model fitting for this stage was restricted to experiments conducted under ad libitum food conditions to minimise confounding effects of resource limitation. For larvae, a Gaussian thermal performance curve (Equation 8) was used to estimate the thermal optimum, as this model provides a stable description of unimodal thermal responses when data near upper thermal failure are limited.
Equation 8
where r(T) is the development rate, T is temperature, rmax is maximum rate at optimum temperature, Topt is the optimum temperature, and a scales the full curve width. The model parameters rmax, Topt, and α were estimated by fitting the model to the empirical data, resulting in values of 0.102, 20.583, and 6.705, respectively.
Several alternative non-linear thermal performance models (including Logan, Lactin, Brière, and Sharpe–Schoolfield formulations) were evaluated for all stages. However, these models explicitly estimate upper critical thermal limits and require empirical observations of declining development rates at high temperatures to produce identifiable and biologically meaningful parameter estimates. Because such declines were not observed for egg and pupal stages, and were only weakly represented for larvae, parameters related to upper thermal limits were not statistically identifiable and resulted in unstable estimates. Consequently, these non-linear models were not retained for inference.
Upper critical thermal limits (CTmax) could therefore not be empirically estimated from the available data and were treated as calibration parameters in subsequent simulations. This modelling strategy ensures that parameter estimates are supported by the experimental data and avoids extrapolation beyond the observed temperature range (Fig.
In addition to temperature, the growth of eggs will be influenced by the relative humidity. The linear degree-day relationship estimated for eggs is assumed to be valid for a relative humidity of approximately 65% (as eggs in the study of
Equation 9
where r(T) is provided by Equation 7 with parameters from Table
Equation 10
Centering the effect at 65% RH, the change in development rate due to relative humidity can be approximated as:
Equation 11
where r(T)=a×(T-T0) is the temperature-driven linear degree-day rate. This formulation allows the combined effect of temperature and humidity on egg development to be consistently incorporated into the degree-day framework.
In addition to temperature, the growth of larvae will be influenced by the aphid biomass consumed/prey density. In extreme situations, first instar larvae will die after one consecutive day of starvation, while the longevity of second and third instar larvae under starvation conditions will be set to two and three days, respectively. These assumptions are based on the starvation experiment conducted by
We assume that the dependence on the number of aphids consumed (Fig.
To combine the prey limitation with the Gaussian temperature response, we define a multiplicative scaling factor f(Bc) (Equation 12) relative to the ad libitum biomass Bcmax. We will define Bcmax based on the maximum number of aphids consumed in the experiment of
Equation 12
The combined larval development rate as a function of temperature and consumed aphid biomass is then (Equation 13, Equation 14):
Equation 13
Equation 14
At Bc = Bcmax, the factor f(Bc) = 1 and r(T, Bc) = r(T), recovering the Gaussian thermal performance curve fitted under ad libitum conditions. At lower aphid biomass, the development rate will decrease proportionally, reflecting prey limitations. This formulation allows larval development to be simulated as a function of both temperature and prey biomass, while explicitly acknowledging that the prey limitation effect was measured at 20 °C and extrapolated to other temperatures (Fig.
Dependence of Sphaerophoria scripta larval development rate on temperature and aphid biomass consumed daily. A family of Gaussian curves describing temperature-dependent development rate is shown for daily aphid biomass consumption [mg] ranging from 1 to Bcmax = 21.59 mg, corresponding to mean larval food intake under constant, non-limiting food conditions in the experiment of
To account for individual variability, a stochastic component will be incorporated, allowing developmental duration to fluctuate within ± 10% of the maximum developmental rate. The total larval developmental period will be partitioned into three instars, allocated as 25%, 25%, and 50% of the total duration, respectively, in accordance with
Given that S. scripta larvae are generalist predators, no preference for specific aphid species is assumed. Larvae are assumed to attack aphids opportunistically, while differences in realised biomass consumption among aphid species arise from nutritional quality rather than prey choice. Consequently, the number of aphids of various species present within each 10 × 10 m2 landscape grid cell will be converted into total available aphid biomass, using species-specific biomass values provided in Table
Re-calculation of different aphid species to biomass (in mg). Scaling factors were calculated comparing the total number of aphids of different types consumed during Sphaerophoria scripta larval development when food was provided ad libitum (see Table
| Aphid species | Aphid instar | Reference | |||
|---|---|---|---|---|---|
| I | II | III early | III late | ||
| Acyrthosiphon pisum | 0.07 | 0.18 | 0.51 | 1.27 | |
| Aphis craccivora | 0.03 | 0.07 | 0.19 | 0.48 | |
| Aphis fabae | 0.04 | 0.12 | 0.33 | 0.82 | Recalculated from A. pisum using scaling factor from Table |
| Myzus persicae | 0.03 | 0.08 | 0.24 | 0.59 | |
| Brevicoryne brassicae | 0.03 | 0.09 | 0.24 | 0.60 | |
| Hyalopterus. pruni | 0.07 | 0.17 | 0.48 | 1.21 | |
| Nasonovia ribisnigri | 0.03 | 0.07 | 0.20 | 0.51 | |
Using species-specific biomass values from Table
Aphid biomass consumption patterns for Sphaerophoria scripta generated based on published studies on S. scripta (
The empirical pattern of aphid biomass consumption across larval development, derived from
Equation 15
where Bcr is aphid biomass [mg] required daily based on the development percentage, and Dper is percentage of larval development. An offset of 2.30 is applied to account for non-zero aphid consumption of one day larvae. In the model, the developed percentage from the preceding day will be utilised to calculate the requisite aphid biomass for the current day.
S. scripta is strictly diurnal, with adults active only in daylight hours (
There are no published studies measuring an intrinsic circadian clock in Sphaerophoria itself, but data from related hoverflies imply a robust endogenous rhythm. For example, Eristalis hoverflies remained continuously active throughout the 12-hour light phase of a 12L:12D cycle, and showed only minimal increases in night time activity when lights were briefly turned on; importantly, this did not shift their next-day activity peak (
Ambient temperature plays a critical role in modulating the diurnal activity patterns of hoverflies. Field observations of syrphid species indicate that activity is predominantly concentrated within a moderate thermal range of approximately 15–25 °C, with minimal activity recorded below 8–10 °C, suggesting a lower thermal threshold near 10 °C (Gilbert 1985). Conversely, peak activity levels are typically observed at higher temperatures of 20 °C and higher. In a field study conducted by
Flight activity in hoverflies is further influenced by weather conditions (
We will incorporate weather effects on hoverfly activity through an hourly weather assessment.
Equation 16
With Equation 16, the temperature at which 50% of S. scripta population becomes active is 15 °C, thus higher than the one provided by E. balteatus by
This activity is further restricted to daylight hours only (Fig.
Knowing when a given hoverfly starts and ceases to be active during the day (based on temperature, rainfall and wind profiles during the day), we can calculate the total number of activity hours per day (htot). The total activity hours per day will then be divided into time spent on feeding (hf), resting (hr), and flying (hm) based on proportions provided by
To date, detailed information on the energetics of S. scripta and other hoverfly species remains scarce. The most comprehensive analyses of foraging energetics are available for E. tenax (
Equation 17
where kr is the scaling parameter [J/(s × mg)] and M is the hoverfly mass [mg].
Equation 18
where
Equation 19
where tflightmax is maximum possible time of flight without feeding, Fat% is percentage of fat deposit related to mass, and Efatdensity is the energy density of fat (assumed to be 37 J/mg).
Given the lack of direct measurements for S. scripta, we can estimate its flight and resting energy consumption using an allometric scaling approach. This method applies a mass-dependent scaling law with an exponent b < 1, consistent with empirical findings in insect flight energetics. The scaling relationship is expressed as (Equation 20):
Equation 20
where MR is metabolic rate, and M is body mass.
As data on the body mass of adult S. scripta are scarce (with only one study of
Equation 21
where L is body length (mm), and a and b are scaling constants. Using E. balteatus as a reference species, with a reported mean body mass of 22.3 mg (
Assuming an allometric scaling exponent of approximately 0.85 (which is typical for flying insects) in Equation 19, and using a mean body mass of 149 mg for E. tenax females (based on field-collected specimens,
To estimate the maximum possible daily energy gain (Emax) and, consequently, the resting energy consumption rate (Cr), the maximum starvation time (tstarvationmax) and the maximum possible time of flight without feeding (tflightmax) need to be assessed for S. scripta.
Equation 22
If we further assume that tstarvationmax for E. balteatus is valid for a hoverfly of mean body mass of 22.3 mg (
If we assume that body mass of S. scripta can vary between 6.6 and 33.3 mg (see above), we can estimate the maximum possible daily energy gain Emax of S. scripta as varying from 14.8 J to 96.1 J depending on body mass (with a mean of 43.3 J for a mean body mass of 16.5 mg), assuming fat deposit of 5% (the same as in E. balteatus,
On the other hand, maximum nectar intake per foraging bout is constrained by the crop capacity.
Equation 23
This equation gives us gut volumes for S. scripta between 1.08 and 3.62 µl across a body mass range of 6.6−33.3 mg (with a mean value of 2.14 µl for a hoverfly with a body mass of 16.5 mg).
The maximum gut fill can be translated into the maximum energy per gut fill Emax(Gv) (reflecting the instantaneous energy intake capacity per feeding event), based on nectar sugar concentration (Equation 24):
Equation 24
where ρsolution is the density of the sugar solution (depends on concentration, ~1.0–1.4 mg/ µl), Csugar is the sugar mass fraction (e.g., sugar concentration of 30% = 0.30 g sugar per g solution), esugar is energy content of sugar (assumed to be 17 J/mg), and ηassim is the assimilation efficiency (if all of the energy ingested is absorbed, then ηassim = 1).
Assuming a mean gut volume of 2.14 µl (for S. scripta with a mean body mass of 16.5 mg), the maximum energy per gut fill Emax(Gv), calculated for a 50% sugar concentration (ρsolution = ~ 1.23 mg/µl) and an assimilation efficiency of 1, is estimated at 22.4 J.
The observed difference between the maximum possible daily energy gain Emax and the maximum energy per gut fill Emax(Gv) is expected because Emax integrates longer-term energy reserves (fat), whereas Emax(Gv) reflects only short-term carbohydrate intake. For energy-budget modelling, this distinction is crucial: Emax(Gv) constrains the instantaneous rate of energy acquisition and thus short-term activity patterns, while Emax defines the maximum daily energy allocation potential, including contributions from stored reserves. Comparing these two metrics allows estimation of gut-filling frequency necessary to sustain activity (Emax / Emax(Gv) ≈ 2 gut fills/day in case of S. scripta of 16.5 mg body mass feeding on nectar with 50% sugar concentration) and provides a framework for modelling trade-offs between feeding, flight, and reproductive investment under varying ecological conditions.
Female Sphaerophoria require pollen to mature their ovaries. As in other syrphids, newly emerged females are not sexually mature until they have fed on pollen (
To our knowledge, detailed information on the nectar preferences of S. scripta, particularly regarding sugar concentration preferences, is lacking. Gilbert (1981) investigated the sucking and ingestion rates of sugar solutions ranging from 10% to 67% in various hoverfly species, including two aphidophagous ones, Syrphus ribesii (Linnaeus, 1758) and Scaeva pyrastri (Linnaeus, 1758). For both species, sucking rates are at the level of around 0.3–0.4 µl per second for sucrose concentrations between 10 and 50%, and then drops with further increase of sucrose concentration (Fig.
Adults are flower-visiting generalists (
Summary of studies providing data on the total number of aphids consumed by Sphaerophoria scripta larvae during development. * To calculate the scaling factor, a base for Acyrthosiphon pisum was set to 154 aphids (mean value from those reported by
| Aphid species | Total number of aphids consumed | Reference | Scaling factor (compared to A. pisum)* | |
|---|---|---|---|---|
| Range | Mean | |||
| Acyrthosiphon pisum | 129 | 129 | 1.0 (base) | |
| Acyrthosiphon pisum | 167–192 | 179 | ||
| Aphis fabae | 190–306 | 234 | 1.5 | |
| Myzus persicae | 300–365 | 333 | 2.2 | |
| Brevicoryne brassicae | 326 | 2.1 | ||
| Hyalopterus pruni | 96–226 | 162 | 1.1 | |
| Nasonovia ribisnigri | 385** | 2.5 | ||
Example of some plant species visited by Sphaerophoria scripta (
| Species | Genus | Family |
|---|---|---|
| Achillea millefolium | Achillea | Asteraceae |
| Aegopodium podagraria | Aegopodium | Apiaceae |
| Agrimonia eupatoria | Agrimonia | Rosaceae |
| Allium scorodoprasum | Allium | Amaryllidaceae |
| Anethum graveolens | Anethum | Apiaceae |
| Anthemis arvensis | Anthemis | Asteraceae |
| Anthericum ramosum | Anthericum | Asparagaceae |
| Anthriscus sylvestris | Anthriscus | Apiaceae |
| Aphanes spp. | Aphanes | Rosaceae |
| Aristolochia spp. | Aristolochia | Aristolochiaceae |
| Asphodelus spp. | Ashpodelus | Xanthorrhoeaceae |
| Aster spp. | Aster | Asteraceae |
| Borago officinalis | Borago | Boraginaceae |
| Brassicaceae spp. | Brassicaceae | |
| Calendula officinalis | Calendula | Asteraceae |
| Calluna vulgaris | Calluna | Ericaceae |
| Calystegia spp. | Calystegia | Convolvulaceae |
| Campanula patula | Campanula | Campanulaceae |
| Campanula spp. | Campanula | Campanulaceae |
| Cardueae spp. | Cardueae | Asteraceae |
| Carum carvi | Carum | Apiaceae |
| Centaurea cyanus | Centaurea | Asteraceae |
| Centaurea jacea | Centaurea | Asteraceae |
| Centaurea nigra | Centaurea | Asteraceae |
| Centaurea scabiosa | Centaurea | Asteraceae |
| Centaurium spp. | Centaurium | Gentianaceae |
| Centranthus spp. | Centranthus | Valerianaceae |
| Cichorioideae spp. | Cichorioideae | Asteraceae |
| Cirsium arvense | Cirsium | Asteraceae |
| Cistus monspeliensis | Cistus | Cistaceae |
| Clinopodium vulgare | Clinopodium | Lamiaceae |
| Convolvulus arvensis | Convolvulus | Convolvulaceae |
| Coronilla varia | Coronilla | Fabaceae |
| Corrigiola telephiifolia | Corrigiola | Caryophyllaceae |
| Crassula | Crassula | Crassulaceae |
| Crepis capillaris | Crepis | Asteraceae |
| Daphne gnidium | Daphne | Thymelaeaceae |
| Daucus carota | Daucus | Apiaceae |
| Dracocephalum moldavica | Dracocephalum | Lamiaceae |
| Echium spp. | Echium | Boraginaceae |
| Echium vulgare | Echium | Boraginaceae |
| Epilobium hirsutum | Epilobium | Onagraceae |
| Erica cinerea | Erica | Ericaceae |
| Erica tetralix | Erica | Ericaceae |
| Erigeron annus | Erigeron | Asteraceae |
| Eucalyptus spp. | Eucalyptus | Myrtaceae |
| Euphorbia spp. | Euphorbia | Euphorbiaceae |
| Foeniculum vulgare | Foeniculum | Apiaceae |
| Fumaria spp. | Fumaria | Papaveraceae |
| Galium mollugo | Galium | Rubiaceae |
| Galium verum | Galium | Rubiaceae |
| Gentiana cruciata | Gentiana | Gentianaceae |
| Geranium spp. | Geranium | Geraniaceae |
| Hedera helix | Helix | Araliaceae |
| Helianthemum grandiflorum | Helianthemum | Cistaceae |
| Helianthemum nummularium | Helianthemum | Cistaceae |
| Heracleum sphondylium | Heracleum | Apiaceae |
| Hypericum perforatum | Hypericum | Hypericaceae |
| Hypericum spp. | Hypericum | Hypericaceae |
| Hypochaeris radicata | Hypochaeris | Asteraceae |
| Inula salicina | Inula | Asteraceae |
| Jasione | Jasione | Campanulaceae |
| Juniperus | Juniperus | Cupressaceae |
| Knautia arvensis | Knautia | Dipsacaceae |
| Lactuca serriola | Lactuca | Asteraceae |
| Lamium album | Lamium | Lamiaceae |
| Lavandula angustifolia | Lavandula | Lamiaceae |
| Leontodon autumnalis | Leontodon | Asteraceae |
| Leontodon hispidus | Leontodon | Asteraceae |
| Leontodon saxatilis | Leontodon | Asteraceae |
| Leucanthemum vulgare | Leucanthemum | Asteraceae |
| Linum catharticum | Linum | Linaceae |
| Lonicera periclymenum | Lonicera | Caprifoliaceae |
| Lotus corniculatus | Lotus | Fabaceae |
| Lycopus europaeus | Lycopus | Lamiaceae |
| Malva moschata | Malva | Malvaceae |
| Malva sylvestris | Malva | Malvaceae |
| Medicago lupulina | Medicago | Fabaceae |
| Melampyrum nemorosum | Melampyrum | Orobanchaceae |
| Mentha spp. | Mentha | Lamiaceae |
| Myosotis arvensis | Myosotis | Boraginaceae |
| Olea europaea | Olea | Oleaceae |
| Origanum vulgare | Origanum | Lamiaceae |
| Papaver rhoeas | Papaver | Papaveraceae |
| Pastinaca sativa | Pastinaca | Apiaceae |
| Pilosella officinarum | Pilosella | Asteraceae |
| Pimpinella saxifraga | Pimpinella | Apiaceae |
| Pinus pinaster | Pinus | Pinaceae |
| Plantago lanceolata | Plantago | Plantaginaceae |
| Plantago suma | Plantago | Plantaginaceae |
| Poaceae spp. | Poaceae | Poaceae |
| Polygonum aviculare | Polygonum | Polygonaceae |
| Potentilla argentea | Potentilla | Rosaceae |
| Potentilla erecta | Potentilla | Rosaceae |
| Potentilla reptans | Potentilla | Rosaceae |
| Quercus spp. | Quercus | Fagaceae |
| Ranunculus acris | Ranunculus | Ranunculaceae |
| Ranunculus bulbosus | Ranunculus | Ranunculaceae |
| Ranunculus repens | Ranunculus | Ranunculaceae |
| Raphanus raphanistrum | Raphanus | Brassicaceae |
| Rhinanthus | Rhinanthus | Orobanchaceae |
| Rhinanthus major | Rhinanthus | Orobanchaceae |
| Rubus spp. | Rubus | Rosaceae |
| Rubus spp. | Rubus | Rosaceae |
| Rumex spp. | Rumex | Polygonaceae |
| Salvia verticillata | Salvia | Lamiaceae |
| Sanguisorba spp. | Sanguisorba | Rosaceae |
| Saxifraga aizoides | Saxifraga | Saxifragaceae |
| Senecio jacobaea | Senecio | Asteraceae |
| Sinapis arvensis | Sinapis | Brassicaceae |
| Sonchus arvensis | Sonchus | Asteraceae |
| Stellaria graminea | Stellaria | Caryophyllaceae |
| Succisa pratensis | Succisa | Caprifoliaceae |
| Teucrium chamaedrys | Teucrium | Lamiaceae |
| Thymus pulegioides | Thymus | Lamiaceae |
| Thymus vulgaris | Thymus | Lamiaceae |
| Tribulus spp. | Tribulus | Zygophyllaceae |
| Trifolium campestre | Trifolium | Fabaceae |
| Trifolium medium | Trifolium | Fabaceae |
| Trifolium pratense | Trifolium | Fabaceae |
| Ulex gallii | Ulex | Fabaceae |
| Ulex minor | Ulex | Fabaceae |
| Verbascum chaixii | Verbascum | Scrophulariaceae |
| Veronica teucrium | Veronica | Plantaginaceae |
| Vicia sativa | Vicia | Fabaceae |
| Viola arvensis | Viola | Violaceae |
Experiments with floral resources have shown that hoverfly flower choice is influenced by flower colour, shape, and abundance. A study on S. rueppellii by
Since foraging movements are intertwined with reproduction and dispersal, we treat them under the heading ‘Dispersal’ below.
The amount of pollen, nectar, and sucrose concentration available to S. scripta from each habitat patch in the landscape per day will be modelled in ALMaSS using the floral resource models. The floral resource models have been developed within the B-GOOD Horizon 2020 project (Ziółkowska et al., unpublished). The framework integrates data on the amount of pollen, nectar, and sugars produced by a single flower/inflorescence of a given plant species with information on flower/inflorescence abundance (i.e. density of flowers/inflorescences per unit area), flowering phenology, plant composition of the habitat, and habitat composition and configuration within the landscape. This approach enables prediction of the spatio-temporal availability of floral resources across different habitat types and landscapes.
The amount of pollen and nectar available to S. scripta in the landscape will be limited to those plants visited only by S. scripta. Such a list of plants will be available based on analysis of plant-pollinator interactions. Table
When foraging, a hoverfly will perceive the landscape as consisting of patches of different landscape elements. All vegetated patches are attributed daily with the amount of floral resources provided by different plants composing those patches. The local perception range for resources is assumed as 150–200 m, similar to the perception range for E. balteatus provided by
In addition, the daily pollen attractiveness Ph of a given habitat patch h will be calculated by multiplying the amount of pollen resources P available to S. scripta from each plant p in the patch on day d by the plant’s pollen preference score ps (Equation 25). The amount of pollen resources produced by plant p on day d in habitat patch h results from the daily pollen production of the plant, the proportion of the plant in the habitat patch and the area of the habitat patch. The pollen preference score ps of a plant is a pollinator-specific measure defined on a semi-quantitative scale from 0 to 3. It is being developed within the Better-B Horizon Europe project and is intended to be linked to the floral resource models of the ALMaSS modelling framework. The pollen preference score was originally developed for bees and is based on documented plant-pollinator interactions, along with the nutritional and chemical properties of pollen, including the protein-to-lipid (P:L) and potassium-to-sodium (K:Na) ratios. While pollen nutritional traits are known to influence pollen selection in bees, no empirical studies are currently available that directly link pollen nutritional composition to pollen preference in hoverflies. Consequently, for S. scripta, the pollen preference score is presently derived solely from documented plant-hoverfly interaction data, reflecting whether a given plant species is known to be used as a pollen source. The integration of additional modifiers relevant to hoverflies (e.g. flower colour, floral morphology, or pollen accessibility) is under development and will be incorporated into future model versions once sufficient empirical evidence becomes available.
Equation 25
The daily pollen attractiveness Ph of a given habitat patch h in a landscape will be further scaled by the nectar attractiveness Nh to obtain the daily food attractiveness Fh of the patch (Equation 26). Scalars cp and cn, for the pollen and nectar attractiveness components, will be calibrated parameters.
Equation 26
The daily nectar attractiveness of a given habitat patch Nh will combine the total amount of nectar produced by each plant species with the relative preference for sucrose concentration, modelled with constrained Gaussian model on observed ingestion rates of S. ribesii, a closely related aphidophagous species in terms of preferred habitats (meadows, grasslands, crop fields) and egg-laying preferences (herbaceous plants, crops), across a gradient of sucrose concentrations (Equation 27):
Equation 27
where Ni is the total nectar amount (mg/day) produced by plant species i in a patch, Si is sucrose concentration (%) of nectar from species i, and w(Si) is weight assigned to sucrose concentration, modelled by the constrained Gaussian ingestion function I(Si) (Equation 28):
Equation 28
Equation 29
Parameters a = 179.73, b = 48.84 and c = 21.98 for Equation 29 were derived from the best-fit ingestion model (R2 = 0.93) to data on S. ribesii from Gilbert (1981) (Fig.
The daily food attractiveness Fh of a patch will be used to drive the long-distance movement between floral patches (see section ‘Dispersal’ for details).
Furthermore, multiple feeding bouts (i.e., discrete foraging events during which the hoverfly fills its gut to its maximum capacity Gv, after which it leaves the flower patch or reduces intake until the gut is sufficiently emptied to resume feeding) need to be considered during the day. In reality, hoverflies will combine foraging and reproduction and integrate these activities together. From the modelling perspective, this integration is not easy, so we suggest viewing this as maximum of Nf feeding bouts where the maximum intake of nectar is limited by the gut volume (Equation 23). During a foraging bout, the hoverfly will attempt to fill its gut to maximum capacity. Each feeding bout can be then translated to the maximum energy per gut fill Emax(Gv), depending on sugar concentration in nectar (Equation 24). The actual energy gain during a feeding bout will be, however, a difference between potential energy gain per bout and the energy loss per bout associated with local foraging movements and flower handling (see ‘Dispersal’ section for energy budget details).
Number of feeding bouts actually performed during a day (Nreal) will be restricted by a time spent on each foraging bout tsbout (which includes time spent in local foraging flights within the patch and total flower handling time in the bout) and time available for foraging per day (being a fraction of time available for all activities daily; see ‘Diurnal activity’ section for details). The time spent within a patch will be estimated based on the mean foraging speed (see ‘Dispersal’ section), the mean distance between floral units of plant species accepted by S. scripta within the patch, and the number of floral units required to obtain the assumed nectar intake (i.e., to fill the gut). The nectar reward per floral unit will be represented by the mean nectar amount per flower unit across all plant species accepted by S. scripta in the patch. This generalisation is necessary because the model does not operate at the level of individual plants; thus, the specific sequence of floral units visited by an individual cannot be determined.
The daily activity of S. scripta will be simulated as a state-dependent sequence of foraging, dispersal, reproduction, and resting, constrained by both time budgets and energetic state (see ‘Dispersal’ section for details. Foraging will be initiated whenever the current short-term energy level Ecurrent falls below a predefined threshold Eforage_threshold, which will be calibrated as a model parameter.
S. scripta is a highly multivoltine species (
The selection of oviposition sites by aphidophagous hoverflies involves the complex integration of visual, auditory, olfactory, and gustatory stimuli (
S. scripta females lay their eggs individually on leaves or stems close to aphid colonies. This trait minimises larval competition and facilitates access to prey (
The effect of prey density (number per plant) on eggs oviposited per Episyrphus balteatus, Syrphus vitripennis and Eupeodes (Metasyrphus) corollae females per day (A) or daily per plant (B). Based on Wnuk and Starmach (1977) controlled field experiment. The relationships between prey density and number of eggs laid daily or daily per plant follow a similar logarithmic function y = a × lnx +b with parameters provided in Table
According to
As females can lay eggs right up until the day they die (
Aphid density is a key driver of oviposition behaviour in aphid-eating hoverflies. In general, females lay more eggs when aphid colonies are abundant (Fig.
Oviposition behaviour and daily oviposition rate changes with female age.
Female fecundity may also be connected to the diet during their larval stage. In S. rueppellii, individuals that feed on M. persicae and A. nerii had significantly less eggs (25–32) compared to those on a diet on R. padi (50) (
Following Honĕk (1993), we assume that the S. scripta potential fecundity (potential total number of eggs to be laid) depends linearly on female mass and thus is set at the female’s emergence. As data on individual mass and fecundity were not available for S. scripta, we based the linear relationship on the minimum and maximum values reported/estimated in the literature, assuming that the minimum reported mass corresponds to the minimum reported fecundity, and the maximum reported mass corresponds to the maximum reported fecundity (Equation 30). Regarding fecundity, we take the data from
Equation 30
where FT is the potential fecundity of a female, and Mf is the mass of a female.
The actual lifetime egg number laid will depend on environmental conditions (weather experienced), amount of food (pollen) consumed, as pollen is necessary for the maturation of eggs, and availability of oviposition sites (i.e., plants infested with aphids). We will further assume that S. scripta females experience enough mating events during their lifetime to fertilise all the possible eggs to be laid, i.e., the potential fecundity is not decreased because of missed mating. We assume a constant pre-oviposition time of 5 days based on
S. scripta will employ a highly adaptive oviposition strategy; females will prefer to lay eggs in immediate proximity to high-density, young aphid colonies on infested leaves, using both prey-derived semiochemicals and plant volatiles to locate optimal sites. During local movements, females will prioritise oviposition sites with higher aphid densities, as these provide better resources for larval development. Females will only lay eggs when the aphid density at a specific location (in a 10 × 10 m grid cell at which aphid densities are provided) exceeds a predetermined threshold. This behaviour may be influenced by the habitat type, but due to the lack of species-specific data and the generalist feeding behaviour of S. scripta larvae, we assume a constant threshold, expressed as a minimum aphid biomass Ath required for oviposition. Based on
The probability of oviposition site selection will be modelled using a logistic function, which is appropriate for this coarse spatial resolution as it captures a biologically plausible threshold-like response: low-density patches are rarely selected, probability increases steeply after exceeding the minimum biomass, and saturates at high densities. This reflects the adaptive oviposition strategy of syrphids while avoiding unrealistic fine-scale selectivity. The function is expressed as (Equation 31):
Equation 31
where A is aphid biomass (mg per 10 × 10 m cell), Ath is the daily biomass threshold (6.5 mg × ml / f per cell with stochastic variation), A50 is the biomass giving 50% oviposition probability, and k is the steepness parameter.
S. scripta lay eggs individually; however more than one egg can be laid per plant if aphid densities are high (Fig.
The expected daily egg production of a female hoverfly will be modelled as a product of baseline oviposition rate and environmental scaling factors reflecting temperature and photoperiod. Formally, the daily oviposition rate Ed(t, A, T, P), where t denotes the female’s reproductive age in days, A is the aphid biomass available at the oviposition site, T is the ambient temperature, and P is the photoperiod length in hours, is given by Equation 32:
Equation 32
where the first bracketed term represents the baseline daily oviposition under optimal temperature and photoperiod conditions, and fT(T) and fP(P) are scaling factors for temperature and photoperiod, respectively.
The baseline oviposition rate will be composed of a prey-dependent term, fA(A), and an age-dependent shape function, fage(t) (Fig.
Equation 33
where the parameters a = 10.270 and b = 20.841 represent averaged coefficients derived from Wnuk and Starmach (1977) for three hoverfly species: E. corollae, S. vitripennis, and E. balteatus (Table
Parameters for logarithmic functions describing the relationship between aphid colony size (number of aphids per plant) and total number of eggs laid or number of eggs laid per plant per day. Based on Wnuk and Starmach (1977), see Fig.
| Species | Total number of eggs daily | Number of eggs per plant per day | R2 | ||
|---|---|---|---|---|---|
| a | b | a | b | ||
| E. corollae | 10.081 | -18.287 | 0.630 | -1.150 | 0.97 |
| S. vitripennis | 10.284 | -22.915 | 0.641 | -1.427 | 0.93 |
| E. balteatus | 10.446 | -21.322 | 0.652 | -1.333 | 0.98 |
The age-dependent oviposition function, fage(t), describing the temporal pattern of egg-laying over the oviposition period will be modelled using a Gaussian (normal) distribution normalized over the oviposition period, Tovip, to ensure that total eggs sum to the maximum potential egg number (set to 550 eggs after
Equation 34
with Z is defined as (Equation 35):
Equation 35
where the parameters μ = 8.33 and σ = 5 define the peak and spread of the oviposition curve. The peak was set at one-third of the oviposition period, consistent with the pattern observed for S. rueppellii at 25 °C under longer photoperiod (
The baseline oviposition rate is valid for the optimal temperature and photoperiod conditions, and thus will be further multiplied by a scaling factor depending on these variables (Fig.
Equation 36
where
Equation 37
with shape and scale parameters k = 4.321 and λ = 16.991 estimated from the fitting procedure and T' is the temperature that results in the maximum WeibullPDF, i.e., the optimum temperature.
Photoperiod effects on oviposition will be incorporated through the scaling factor fP(P), which linearly scales oviposition between a minimum photoperiod threshold Pmin = 11 hours and a maximum threshold Pmax = 14 hours as (Equation 38):
Equation 38
and is clipped between fmin and 1 to represent biological constraints on egg laying, where fmin is nonnegative and the minimum scaling factor based on photoperiod.
S. scripta is a migratory species (
Several studies suggest that syrphid flies respond most strongly to landscape composition at spatial scales between 500 and 1,500 m (
Perception range in E. balteatus estimated from field observations is 200 m (
The timing of migration is a complex phenomenon influenced by a range of factors, including endogenous mechanisms such as the circadian clock (
We will treat S. scripta as a partially migratory species. Specifically, we assume that the proportion of females from the last autumn generation will exhibit migratory behavior, departing from the local landscape before oviposition. Those which stay will lay eggs which hatch into larvae which, in the last stage, will start the overwintering. A given female from the autumn generation will initiate migration movement with a defined probability pm.
There are two movement types planned for implementation: short-range movement and long-range movement. Short-range movement simulates intensive search behavior when the adult hoverfly scans the local surroundings in search of food (nectar and pollen) and oviposition sites (aphid prey for larvae). Based on foraging speeds reported for honey bees and bumble bees (
To determine whether remaining in a current location for foraging is energetically profitable for S. scripta, the balance (Equation 39) between potential energy gain per bout (gut-limited) (Equation 40) and the energy loss per bout (Equation 41) associated with local foraging movements (assuming foraging flight speed of 1 m) and flower handling will be evaluated:
Equation 39
where:
Equation 40
where Emax(Gv) is maximum energy that can be stored in the crop per bout (Equation 24), ϵf is hoverfly foraging efficiency (fraction of available resources acquired based on visitation and handling, calibrated parameter), rp is perception range, Npatch is patch-level nectar production (in mg/m2/day) by plants accessible by S. scripta, tsbout is time spent in a patch (where ts = time spent in local foraging flights within the patch tlocal_fligh + total flower handling time in the bout thandle) and hf is time within a day spend on foraging (calculated based on weather conditions and photoperiod, see section ‘Diurnal activity’).
Equation 41
where Cf is flight energy consumption rate and Crest is energy consumption when resting/handling on flowers (see ‘Foraging’ section).
A patch will be deemed profitable if the daily energy that can be obtained from accessible nectar sources exceeds the energy required for local search flights within the perceptual range (assuming, for simplicity, that energy gain comes only from nectar). This approach ensures that S. scripta preferentially remains in patches where resource availability is sufficient to offset the energetic cost of local search, and otherwise engages in long-range movements to locate more rewarding habitat. The long-range foraging movement will be restricted by a maximum daily dispersal ability and can be carried out in Nf movement bouts. This movement is driven by the availability and distance to foraging resources. The maximum daily dispersal ability Dtmax (for movements between floral patches) will be calculated from the available daily flight time (hm) and the flight speed v. The maximum distance achieved during one bout will be restricted by available usable energy calculated based on percentage of stomach filling (Table
Flight energy budget and flying capacity of Sphaerophoria scripta provided for an individual of a mean body mass of 16.5 mg. For local search movement a speed of 1 m/s is assumed, while for long distance movement the maximum speed of 7.8 m/s. The maximum flying speed can only be achieved for short time periods.
| Nectar glucose [%] | Usable energy [J/µL] | Full stomach usable energy [J] | Max flight time [min] | Local search distance [m] | Long movement distance [m] |
|---|---|---|---|---|---|
| 20 | 0.6 | 1.3 | 9.3 | 558 | 4352 |
| 50 | 1.56 | 3.34 | 24.1 | 1446 | 11279 |
When dispersing for oviposition sites, a hoverfly will be driven by aphid density / aphid biomass updated in a landscape daily with a resolution of 10 × 10 m. Within the perception range a hoverfly (the same as for foraging) will be capable of performing local search movements for cells providing a minimum aphid density / aphid biomass needed for larvae to survive (see section ‘Reproduction and oviposition’). During this local search, energy will be spent in a similar way as described above for foraging. If not enough aphids are available locally, then hoverfy switches to long-range movement, occurring with similar rules as long-range movement for foraging patches.
Dispersal activity will be tracked individually for each hoverfly, both in terms of time and energy spent and distance travelled, and once daily limits are reached a hoverfly will suspend its activity for that day. Importantly, daily time available for flying (hm) includes long-range movements for both foraging and oviposition sites.
In the model, a hoverfly will switch between four behavioral states – foraging, flying/dispersing, reproduction, and resting – according to a state-dependent energy budget. Energy reserves will be represented at the individual level and divided into:
The model will simulate daytime activities under time and energetic constraints, with behavioral decisions depending on internal energy state, resource distribution, and movement costs.
The daily activity budget will be divided based on observations of
Each activity (flying, foraging, reproduction, and resting) will consume energy at a rate dependent on body mass. Cost of flying activities will be calculated as (Equation 42):
Equation 42
where hm is time spend on flying.
During a foraging bout, the hoverfly will attempt to fill its gut to maximum capacity with the potential energy gain per bout depending on nectar sugar concentration (Equation 40). The total daily nectar intake will be constrained by gut-emptying time (tempty), determining the maximum number of bouts per day (Nmax).
Egg maturation requires pollen ingestion, modelled as a daily pollen intake threshold (Pthreshold) before oviposition can begin. Once mature eggs are available and Ecurrent exceeds an oviposition energy threshold (Eovip), the hoverfly switches to searching for oviposition sites.
The energy cost of oviposition will be calculated as (Equation 43):
Equation 43
where Neggs,laid is number of eggs laid per day, an Eegg is energy needed for laying an egg (~0.05–0.2 J/egg, based on lipid- protein content of syrphid eggs; estimation from aphidophagous species). Maximum daily egg-laying rate is imposed as an additional stopping rule.
Resting will occur when all other activities are completed or constrained by time budgets. The resting metabolic cost will be calculated as (Equation 44):
Equation 44
where hr is time spend on resting.
At the end of each day, remaining energy will be computed as (Equation 45):
Equation 45
where Egut is energy remaining in the gut (if feeding ended late), Eunused_eggs = (Eggsmature – Eggslaid) × Eegg, assuming non-laid eggs are reabsorbed and converted to fat (similar assumption as in
Then, the daily fat balance will be updated as (Equation 46):
Equation 46
where Fatreserve(t) is the reserve level at the start of day t, and Fatreserve(t+1) is the updated level for the following day. When the daily energy balance Eend exceeds the threshold Ethreshold, the surplus is stored as fat, increasing Fatreserve. Conversly, when Eend is below the threshold, fat reserves are mobilized to cover the deficit, decreasing Fatreserve. This formulation ensures that fat reserves function as a dynamic energy buffer, capable of both recovery and depletion depending on the daily energy balance.
The energy available at the start of the next day will be calculated as (Equation 47):
Equation 47
where αmobil is the fraction of fat that can be mobilized overnight, and Ebaseline is the minimum short-term energy level (sugar pool) that a hoverfly naturally maintains overnight or at rest, even without recent feeding (it will be a calibrated parameter).
This structure allows day-to-day feedback, with reproductive output and survival probability depending on the previous day’s energetic balance.
In the model, a hoverfly will switch between the foraging and oviposition behavior once enough energy is gained from nectar consumption and enough pollen is consumed for egg maturation. Thus, two thresholds will be introduced, one for percentage of filling of the stomach needed for oviposition expressed in energetic terms (Eovip_threshold, calibrated parameter), and a second related to pollen consumption (Pthreshold). Here we assume that there is a certain amount of pollen needed for maturation of a single egg (Pegg, calibrated parameter). Thus if, for a given day, we know a daily egg production rate, we know how much pollen needs to be consumed to allow the eggs to mature. Only if this is achieved, and if enough energy has been obtained, can a female switch to reproductive behavior. We assume that pollen can be consumed at the same time as nectar. As pollen intake rate is unknown, this will be a calibrated parameter in the model, allowing to scale the amount of pollen consumed with the time a hoverfly spends in a given location, assuming a certain amount of pollen is available within the perception range of a hoverfly.
Four types of dispersal actions will be considered:
We plan to represent the movement using the following rules:
This behavior requires the specification of two functions, one for oviposition site acceptance and one for foraging site acceptance. The first is given by Equation 31, and the latter is related to assessment of patch profitability (Equation 39). At each step, the current level of energy Ecurrent is evaluated, i.e., flying energy cost is subtracted after each flight (inter-patch or to oviposition sites), and reproduction cost is subtracted after each egg laying. Thus, if Ecurrent falls below forage threshold during oviposition or dispersal, a hoverfly will switch back to foraging.
The above logic does not include hibernation and migration behaviors. Individuals from the last autumn generation will be assigned to one of two seasonal strategies, depending on a migration probability (pm): (i) migration mode or (ii) overwintering/hibernation mode, producing a larval overwintering generation. In migration mode, reproduction is halted; unlaid eggs are reabsorbed, and their energy is converted into fat. Foraging is directed exclusively toward sugar intake to build long-term energy reserves until a fat threshold is reached. Once this threshold and appropriate environmental conditions (e.g., a photoperiod threshold) are met, the hoverfly migrates (and is removed from the landscape). In overwintering/hibernation mode, individuals continue to follow the standard logic, ovipositing until the daily maximum egg-laying potential is reached or until energy constraints prevent further reproduction.
S. scripta does not typically overwinter as an adult but instead survives winter conditions predominantly during an immature stage. In temperate regions, individuals have been reported to overwinter mainly as late third-instar larvae buried in soil or leaf litter, resuming development after spring warming (
Overwintering larvae of aphidophagous hoverflies, including S. scripta, typically occupy sheltered terrestrial microhabitats that offer thermal stability and protection from environmental stressors. The common overwintering sites are within the leaf litter, among grass tussocks, or at the soil-litter interface in habitats such as field margins, hedgerows, and woodland edges. However, in the study of
Larvae are usually found at shallow depths, ranging from the surface to approximately 3–5 cm into the soil, where decaying plant material or moist detritus provides insulation and high humidity. These microhabitats buffer larvae against freezing conditions and may facilitate supercooling or freeze tolerance.
Unfortunately, studies on overwintering regulation in Sphaerophoria species are rare.
In autumn, adult hoverflies preferentially exploit landscape elements with dense and structurally complex vegetation—such as field margins, hedgerows, woodland edges, meadows, extensively managed grasslands, and agricultural fields infested with aphids late in the season—which provide late-season floral resources and aphid-infested host plants, while also incidentally offering suitable microhabitats for overwintering of late-instar larvae or pupae.
Start and end of overwintering will be primarily driven by photoperiod, with temperature factor acting as an additional trigger which may fasten the onset and offset of hibernation. Thus, a threshold date HSdate after which the start of hibernation is mandatory will be applied. This threshold will be set as day in the year at which the photoperiod falls below a certain number of hours (Phstart). However, if S. scripta larva experience cold temperatures earlier, the start of overwintering will come earlier. Thus a certain number of days (Hdays) with minimum night temperatures below a threshold (Thstart) will be required to initiate hibernation of S. scripta. Hdays, Thstart will be initially set to 5 days and 12° C, respectively, and Hdate will be set as date corresponding to photoperiod of 11 h (assumed after E. balteatus).
Offset of hibernation will also be related to photoperiod and temperature. A certain number of days (Edays) with maximum day temperatures above a threshold (Thend) will be required; however, emergence will also be restricted by date, not being earlier than a given day (Edate) corresponding with photoperiod of Phend. Edays and Thend. It will be initially set to 5 days and 10° C, respectively, and Edate will be set as date corresponding to photoperiod of 11 h.
As no data on distribution of individual larvae entering and leaving the hibernation sites is available, we will assume this process to follow a non-linear saturation function, with fast initial increase and gradual slowdown (Equation 48):
Equation 48
where CA(t) is cumulative percentage of individuals entering and leaving habitat site, and k (rate constant) and t (time in days) are parameters which will be fitted in the calibration process.
The mortality of aphidophagous hoverflies during its immature stages is generally high, although exact rates depend on species, and vary depending on habitat conditions, prey availability, and natural enemies. Like other aphidophagous syrphids (e.g. E. balteatus, E. corollae), S. scripta experiences its greatest losses during the egg and early larval stages. Survival rates documented by
Although no specific studies on S. scripta are available, the study of
Aphid type and density seems to be important factor determining mortality at larval stages of aphidophagous hoverflies. Increasing mortality of larvae with decreasing aphid density was reported for E. balteatus (
Another important source of mortality in aphidophagous hoverflies is parasitism. Under certain conditions, field data suggest that the impact of parasitoids on hoverfly populations can be substantial and, in some cases, potentially severe, particularly in intensively managed agricultural landscapes (
Parasitoids of aphidophagous hoverflies such as S. scripta primarily attack the preimaginal stages, including larvae and pupae. Many parasitoid taxa exploit Syrphinae hosts as koinobiont endoparasitoids, laying eggs in or on early larval instars and allowing the host to continue developing for some time before the parasitoid larva consumes it from within (
Parasitoids locate syrphid hosts using chemical cues associated with aphid colonies and the host itself. Volatile aphid-derived odours guide parasitoids to infested plants, while contact cues on the larval cuticle trigger ovipositor insertion. Final host acceptance and oviposition appear to depend on internal cues, likely from larval haemolymph (
Unfortunately, none of the published studies focus exclusively on Sphaerophoria species. Typically, field surveys collect all aphidophagous hoverflies present in a study system, rear them under laboratory conditions, and record the parasitoids that emerge. In many cases, parasitism rates are reported per parasitoid species rather than per host species. When host-specific data are available, the number of Sphaerophoria individuals examined is often very small compared to other hoverfly species, particularly E. balteatus. Consequently, parasitism rates reported for aphidophagous hoverflies are difficult to extrapolate directly to S. scripta. Nevertheless, parasitoid species repeatedly recorded from Sphaerophoria hosts across different studies provide valuable qualitative information on host-parasitoid associations. An overview of parasitoids reported for Sphaerophoria species, together with their mode of action and the developmental stages attacked, is therefore presented in Table
Parasitoids of Sphaerophoria spp., mode of action, and stages attacked.
| Parasitoid species | Family | Mode of action | Stage attacked | Reference |
|---|---|---|---|---|
| Diplazon laetatorius (Fabricius, 1781) | Ichneumonidae (Diplazontinae) | Larval endoparasitoid | Late larva → adult emerges from puparium |
|
| Diplazon pectoratorius (Gravenhorst, 1829) | Ichneumonidae (Diplazontinae) | Larval endoparasitoid | Larva → puparium | |
| Diplazon tetragonus (Thunberg, 1822) | Ichneumonidae (Diplazontinae) | Larval endoparasitoid | Larva → puparium | |
| Diplazon signatus (Fabricius, 1781) | Ichneumonidae (Diplazontinae) | Larval endoparasitoid | Larva → puparium | |
| Enizemum ornatum (Gravenhorst, 1829) | Ichneumonidae | Larval endoparasitoid | Larval instars |
|
| Promethes monticola (Förster, 1869) | Ichneumonidae | Larval endoparasitoid | Larva → puparium | |
| Syrphophilus bizonarius (Gravenhorst, 1829) | Ichneumonidae | Larval endoparasitoid | Larva → puparium | |
| Pachyneuron formosum (Walker, 1833) | Pteromalidae | Pupal endoparasitoid / ectoparasitoid | Pupa (occasionally late larva) |
|
| Pachyneuron grande (Thomson, 1878) | Pteromalidae | Pupal endoparasitoid | Pupa |
|
| Syrphophagus aeruginosus (Dalman, 1820) | Encyrtidae | Larval–pupal endoparasitoid | Larva → puparium |
|
| Cheiloneurus boldyrevi (Trjapitzin, 1963) | Encyrtidae | Pupal endoparasitoid / hyperparasitoid | Pupa | |
| Trichosteresis foersteri (Kieffer, 1907) | Ceraphronidae | Larval endoparasitoid | Larva → puparium |
|
| Lygocerus sp. (Förster, 1869) | Ichneumonidae | Larval endoparasitoid | Larva → puparium |
Background mortality will be defined separately for the egg-to-pupa stages. This mortality is a daily probability applied at the start of each daily time step. For all the immature stages of S. scripta, this background mortality probability will depend on both temperature and humidity and will be calculated based on the polynomial regression models fitted to the mortality data on immature stages of S. rueppellii (
Impact of temperature and relative humidity (RH) on mortality of immature stages of Sphaerophoria rueppellii: (A) egg, (B) larva, (C) pupa. Points represent measurement data from experiments of
Equation 49
The effects of aphid species and prey density on larval mortality will not be included in the model directly. The influence of aphid species has only been investigated for a limited number of taxa (R. padi, M. persicae, and A. nerii), and remains uncharacterised for other aphid species. Furthermore, unlike findings reported for other aphidophagous syrphids such as E. balteatus, the effect of aphid prey density on larval mortality in Sphaerophoria species has not been confirmed. In the only study conducted on S. rueppellii, no significant relationship was observed. We will, however, include a density-dependent mortality factor refelecting the competition among larvae and possible cannibalism. Density dependence will be introduced by limiting the number of S. scripta that could be present in a surrounding of any larva, to a fixed number of larvae. Additional larvae will be removed from the simulation (died because of food limitation, or eaten). The size of the surrounding will be defined separately for each larval instar, reflecting their increasing mobility with age.
In addition to the background and density-dependent mortality, parasitism-induced mortality will be incorporated as a distinct process acting on immature stages of S. scripta. Aphidophagous hoverfly parasitoids typically oviposit into late larval instars, but host mortality is delayed, with parasitised larvae continuing to feed, grow, and pupate normally before dying at or shortly before adult emergence. To reflect this biology, parasitism will not be implemented as an immediate stage-specific mortality factor.
Parasitism will be modelled as a two-step process. Individuals reaching susceptible larval stages (late second and third instars) are assigned a baseline daily parasitism probability (ppara0), derived from cumulative parasitism rates (Ppara) observed over n days of larval susceptibility (Equation 50):
Equation 50
Because species-specific parasitism rates for S. scripta are largely unavailable, the cumulative parasitism rate used in the model will be based on values reported for D. laetatorius, one of the most common and consistently reported parasitoids of Sphaerophoria species (Table
The effective daily parasitism probability (pparaL) will be then adjusted for landscape-dependent variation (Equation 51):
Equation 51
where (L) is a dimensionless modifier reflecting habitat complexity (L > 1) in simplified landscapes, (L < 1) in complex landscapes. Parasitised larvae develop normally, with no reduction in aphid consumption, and all parasitised individuals experience mortality at the pupal-adult transition, representing successful parasitoid development and emergence from the host puparium.
This formulation allows parasitism-induced mortality to be incorporated as a delayed-lethal process, mechanistically distinct from background mortality defined in Equation 49, while enabling modulation of parasitism risk by landscape structure.
To simulate pesticide responses in S. scripta, we adopt a modelling framework analogous to that used in the development of the ApisRAM honey bee colony model (
Equation 52
where PI(t) is the new contamination from intake, PC(t) is from the contact exposure and Po(t) is from the overspray exposure.
Foraging hoverflies may be exposed by collecting pollen and nectar from contaminated flowers. The pesticide amount in the consumed resource is represented by PI(t) and is assumed to move directly to the hoverfly’s body (PN(t)).
The overspray exposure pathways are only relevant to any hoverfly stage present at the moment of pesticide spraying. Contact exposure can occur when a mobile stage moves in a contaminated area. In both cases, a simple one-time absorption model is used; i.e., we assume that the pesticide is absorbed into the hoverfly’s body once, with separate parameters for contact and overspray.
Contact exposure specifically pertains to foraging adults and occurs when a hoverfly touches a contaminated plant surface during foraging. The amount of pesticide transferred to the body through contact is controlled by two user-defined parameters as shown in Equation 53.
Equation 53
where PS is the pesticide amount per square meter on the plant surface, S is a constant representing the area of the hoverfly that is in contact with the surface. Here, we might imagine that foot, abdomen, and wing contact could occur. SC is the absorption rate that determines the amount of pesticide PS that will be transferred to the body. This implementation does not consider foraging time, but both parameters can be adjusted to make this approach more or less conservative.
Overspray exclusively occurs when hoverflies (adults or larvae) are active in a field where simultaneous pesticide spraying occurs and/or where drift occurs in the adjacent area. Two parameters, starting time and ending time, for a pesticide spray event are used to control whether overspray can happen. Overspray can only occur if a hoverfly is in the exact location when the pesticide is being sprayed. When the overspray happens, the contaminated pesticide amount (PO) going to the hoverfly’s body is calculated using Equation 54.
Equation 54
where S represent a proportion of the body surface, as for Equation 28, α is the pesticide spraying application rate, So is the absorption rate for overspray.
To determine the effect of the pesticide body burden, the initial model only considers acute mortality. To do this requires three parameters. The first is a threshold for effect, Pt, above which there is a daily probability of mortality Pm. The third threshold D is the daily decay rate of the pesticide in the hoverfly’s body. This approach will implement a first model for implementing pesticide effects and assumes that an ALMaSS or equivalent landscape model is available to generate the pesticide concentration in the nectar and vegetation, as well as overspray.
There will be a number of other mortalities considered in the model, an important one being the daily background mortality of adult hoverflies. However, empirical data on adult background mortality under natural conditions remain scarce. The only available estimates for Sphaerophoria species derive from laboratory-based studies, where survival was assessed under controlled conditions, often as part of unrelated experimental treatments. For instance,
Despite these findings, extrapolating laboratory-derived survival data from S. rueppellii to estimate background mortality in S. scripta would not be reliable due to interspecific differences, limited sample size (n = 10), and the absence of natural mortality factors such as predation and environmental stressors. Consequently, the model will employ a generalized daily background mortality rate for adult females, treated as a calibration parameter.
Overwintering mortality will be assessed once, at the conclusion of the overwintering period, prior to adult emergence. Given the limited knowledge regarding mortality dynamics during overwintering, this parameter will also be incorporated as a model input.
Additionally, mortality associated with agricultural management practices will be considered. Immature stages of S. scripta occur either on aphid-infested plants (eggs and larvae) or in the soil/near the plant base (pupae). Mortality risk depends on both the spatial location of the stage and its temporal overlap with specific crop operations. Eggs and larvae are only susceptible during the main aphid season, when they feed within colonies on crop plants, whereas pupae may be affected by soil-disturbing operations irrespective of aphid presence. Based on these considerations, Table
Parameters of the polynomial regression models for Sphaerophoria rueppellii mortality at different life stages. Models were fitted based on data from
| Developmental stage | a1 | a2 | a3 | a4 | a5 | a6 | R2 |
|---|---|---|---|---|---|---|---|
| Egg | 0.422 | -19.94 | -0.0074 | -0.0001 | -0.015 | 339.7576 | 0.95 |
| Larva | 0.021 | -2.2875 | -0.0199 | -0.0001 | 0.0247 | 162.6233 | 0.99 |
| Pupa | 0.105 | -4.7375 | -0.0016 | 0 | 0.0057 | 57.2263 | 0.99 |
Agricultural activities that have non-zero probability of mortality in immature stages of Sphaerophoria scripta.
| Activity | Egg mortality | Larva mortality | Pupa mortality | Notes |
|---|---|---|---|---|
| Harrowing | 0 | 0 | 0.5 | Soil disturbance can affect pupae; eggs/larvae absent before sowing |
| Ploughing | 0 | 0 | 0.5 | Soil disturbance pre-sowing; eggs/larvae absent |
| Stubble cultivator | 0 | 0 | 0.5 | Post-harvest soil disturbance; affects pupae |
| Autumn roll | 0 | 0 | 0.5 | Soil compaction/rolling can crush pupae |
| Autumn sowing | 0 | 0 | 0.3 | Minor impact on pupae near surface |
| Bed forming | 0 | 0 | 0.3 | Soil preparation may disturb pupae |
| Bulb harvesting | 0 | 0 | 0.3 | Soil disturbance; pupae may be affected |
| Harvest | 0 | 0 | 0.2 | Minor impact on soil/lower plant pupae |
| Mechanical weeding | 0.3 | 0.3 | 0.2 | Direct disturbance of leaves/aphid colonies; minor pupae disturbance |
We propose a mechanistic, stage-structured model of S. scripta population dynamics that synthesizes temperature-dependent development, prey-specific larval survival, adult nutritional ecology, foraging behaviour and movement into a unified, modular framework. The model presented here is grounded in a relatively substantial body of literature. However, many of the processes incorporated remain characterised by uncertain parameter values or mechanisms. Much of the information informing the model derives from laboratory studies and, in several cases, from studies of other hoverfly species, rather than S. scripta itself. Thus, some crucial information about the species is still missing or uncertain, and here we outline some of the thinking behind our choices.
The available data were insufficient to estimate detailed thermal performance curves for the developmental stages of S. scripta. As a result, temperature-dependent development of eggs and pupae were modelled using linear degree-day relationships fitted to development rates, reflecting the approximately linear response observed within the experimentally tested temperature range. For both stages, data at higher temperatures are lacking, precluding reliable estimation of upper thermal limits. In the pupal stage, the degree-day model suggests a lower developmental threshold of 3.6 °C; however, the associated confidence interval is wide (-7.5 to 8.0 °C), indicating limited information on low-temperature constraints and substantial parameter uncertainty. In contrast, larval development showed a unimodal response to temperature and was therefore modelled using a Gaussian function fitted to development rates under ad libitum feeding conditions. Although this approach better reflects the biological expectation of an optimal temperature, the larval stage remains the most uncertain due to sparse, heterogeneous data. Notably, the primary focus of most existing studies was not the exploration of temperature effects on development, but rather the influence of diet or other ecological factors. These studies often employed single temperatures or narrow thermal ranges, limiting their utility for modelling thermal responses. In addition, although for modelling the temperature-dependent development of larvae, we included only results from studies in which aphids were provided ad libitum, the studies differed in terms of other laboratory settings, resulting in quite a variability of obtained results for the same temperatures. Given that the larval stage appears particularly sensitive to environmental variability, uncertainties in thermal parameters may disproportionately influence predictions of larval development duration.
Larval development in aphidophagous hoverflies is strongly dependent on aphid prey availability. In our model, we assume that prey limitation impacts larval development additively across temperatures. However, the only available empirical data linking prey density and S. scripta larval development were obtained at 20 °C (
Aphid consumption patterns during larval development were drawn from studies on various Sphaerophoria species reared on different aphid species. To facilitate comparisons, we developed a recalculation method converting aphid densities to biomass consumed. Further, we rescaled daily aphid biomass consumption by other Sphaerophoria species to match S. scripta, based on interspecific comparisons of larval mass. These results support the statement by
Empirical data on juvenile survival for S. scripta are sparse. For this reason, we adopted temperature and humidity-related mortality functions fitted to data from S. rueppellii (
Other mortality factors, including overwintering losses, are poorly documented. S. ribesii larvae are known to be strongly freeze tolerant (
The floral preferences of Sphaerophoria species are not well characterised. While our model includes flowering plants documented as pollen and nectar sources for S. scripta in plant-pollinator interaction databases, quantitative information on the relative importance of specific floral traits (e.g. colour or shape) and pollen nutritional requirements remains limited. Experimental evidence from S. rueppellii indicates that hoverfly foraging is influenced by visual floral traits such as colour, shape, and flower abundance (
Several foraging and energy budget parameters were estimated through allometric scaling from other hoverflies. Stomach volume (
Reproductive parameters of S. scripta are likely shaped by energy reserves, nutrient intake, environmental conditions, and prey availability for larvae. Yet, these mechanisms remain largely unquantified. Patterns of daily egg production were derived from S. rueppellii and rescaled to the maximum egg production of S. scripta inferred from
Dispersal functions were designed to integrate with foraging and oviposition behaviours, with daily activities driven by reproductive and foraging objectives. These depend on resource distributions and are limited by S. scripta movement abilities. Model calibration will therefore focus on evaluating behavioural parameters in relation to the spatial and temporal resource patterns generated by the landscape model. Such alignment is essential to ensure that emergent population dynamics realistically reflect field conditions.
Given the ecological significance of migration for S. scripta, we assume that females of the autumn generation may exhibit migratory behaviour with a certain probability. However, as the primary objective of the current model is to inform risk assessment, the probability of migration will be set to zero in the first version of the model. This simplification is intended to prevent the confounding and dilution of potential pesticide effects, thereby enabling clearer interpretation of local risk dynamics.
While the model lacks some of the detailed parameterisation characteristic of other ALMaSS models, it provides a dynamic framework capable of responding to variations in weather, habitat configuration, and resource availability. This first formal implementation serves as a structured synthesis of current ecological knowledge, intended for refinement through post-deployment calibration using a pattern-oriented modelling (POM) approach. Our prior work has demonstrated POM’s utility in improving realism and predictive accuracy in individual-based models of beneficial insects. This model represents a robust starting point for iterative development, designed to facilitate scenario analyses of pesticide effects within managed landscapes.
This section outlines the key assumptions and limitations associated with the design of this model and its integration within social-ecological systems simulations. Following
The S. scripta model synthesises extensive literature, though many processes involve uncertain parameters and mechanisms, primarily derived from laboratory studies and other hoverfly species. The model embodies several critical assumptions and simplifications that constrain its applicability and interpretation.
This model is designed to simulate the population dynamics of aphidophagous hoverflies in temperate European agricultural landscapes, with specific focus on responses to environmental variability, resource availability, and pesticide applications. The parameterisation using S. scripta data makes it most directly applicable to multivoltine syrphid species with similar ecological traits; generalist aphid predators during larval stages, polylectic adult pollinators, and facultative migrants capable of multiple generations per year.
The phenology in the present model is parameterised primarily for northern and central European conditions, where part of the S. scripta population is expected to overwinter at immature stages. However, evidence from emergence-trap studies in agricultural landscapes in south-western and central-western France demonstrate that S. scripta commonly overwinters as pre-imaginal stages and emerges locally in spring (
The ALMaSS framework constrains the model to landscapes typically spanning 100 km2, operating at 1 m2 spatial resolution with daily time steps over multi-year to decadal periods. This scale captures local population dynamics, seasonal migration patterns, and landscape-level resource heterogeneity, but may not fully represent large-scale metapopulation processes or continental migration networks that characterise some hoverfly species. The daily time resolution is appropriate for capturing development, mortality, and movement decisions but cannot resolve within-day behavioural sequences or circadian rhythms in foraging activity.
The sparse data available for the thermal performance relationships in this model mean that care must be taken in overinterpreting temperature-related scenarios, especially if they include extreme temperatures not likely to be well supported by the stage-specific functions used here (linear degree-day models for egg and pupal stages, and a Gaussian thermal performance function for larval development).
Sparse data exists on juvenile survival, with information only available for the related species S. rueppellii. Other mortality drivers are known but not well quantified. Critically, the impact of prey availability on larval mortality is not included in this version of the model due to insufficient data supporting the relationship between prey density and mortality for Sphaerophoria species, unlike findings for other aphidophagous hoverflies such as Episyrphus balteatus.
Many behavioural and physiological patterns are inferred based on data from other species within the genus (such as S. rueppellii) or at the broader level of aphidophagous hoverflies. While such cross-species extrapolation introduces uncertainty where species-specific adaptations may differ significantly from generic patterns, many key traits relevant to population dynamics (e.g. larval aphid predation, pollen dependence for egg maturation, and general phenology) are broadly conserved within aphidophagous Syrphinae. Consequently, this approach also enhances the generality of the model, allowing S. scripta to serve as a representative of the aphidophagous hoverfly guild. Species-specific refinements can be readily implemented through reparameterisation as additional empirical data become available.
The model simulates daytime activities under time and energetic constraints, with behavioral decisions depending on internal energy state, resource distribution, and movement costs. However, several physiological and behavioural parameters, including flight and resting energy expenditure, gut volume, and flight speed, were estimated using allometric scaling approaches. These estimates were derived by comparing body mass or body length of S. scripta with those of closely related syrphid species, introducing compound uncertainties from both the scaling relationships and the source data.
Limited knowledge exists regarding the proportion of populations exhibiting migratory behaviour. The probability of exhibiting migratory behaviour is set as a fitted parameter which, for the sake of simplicity, is assumed to be zero in the first version of the model. This eliminates important population processes that could influence both local dynamics and pesticide exposure patterns.
The model assumes that density dependence operates through two primary mechanisms, the availability of larval habitats and aphid prey availability. This simplified representation may miss other important density-dependent processes such as interference competition, disease transmission, or habitat modification effects.
The model assumes genetically uniform populations with fixed physiological and behavioural parameters. However, S. scripta populations across Europe likely exhibit local adaptations to climate, host plants, and agricultural practices. Genetic variability in thermal tolerance, development rates, or pesticide resistance could influence population responses to environmental stressors. Additionally, the model excludes gene flow between populations, which in highly mobile species like S. scripta could rescue local populations from pesticide impacts or introduce maladapted genotypes.
While the model incorporates nectar concentration preferences and pollen requirements, it simplifies the complex cognitive processes underlying pollinator foraging. Real hoverflies may exhibit flower constancy, learning, or risk-sensitive foraging that optimises energy gain while minimising predation risk. The model treats each foraging decision independently, potentially missing emergent patterns where experience influences subsequent choices or where local depletion of resources creates spatial foraging patterns not captured by simple attractiveness functions.
The model focuses on aphid-hoverfly dynamics but simplifies the broader food web context. Sphaerophoria scripta larvae coexist with other aphid predators (ladybirds, lacewings, parasitoids), and these interactions may involve both competition and niche complementarity. In structurally complex habitats, spatial and temporal partitioning of aphid resources, differences in prey stage use, and behavioural specialisation can promote complementary predator effects, potentially enhancing aphid suppression rather than reducing prey availability. Similarly, adult hoverflies interact with other pollinators in ways that may involve resource competition or facilitation, depending on floral diversity and landscape context, and they themselves serve as prey for spiders, birds, and other predators. Although such multi-trophic and complementary interactions are not explicitly represented in the current model, they may generate indirect effects whereby pesticide impacts on co-occurring predator or pollinator communities secondarily influence hoverfly populations.
The ALMaSS landscape simulation uses a combination of raster and patch representations to map the homogeneous landscape polygons (patches) onto a raster map. This means that, despite 1 m2 resolution, the model treats cells forming landscape polygons as spatially uniform. However, hoverflies respond to microclimatic variation within fields, seeking thermal refugia, exploiting boundary effects, or concentrating in resource-rich patches. Larvae may preferentially occupy specific positions on plants (leaf undersides, stem bases) that offer protection from adverse weather or natural enemies. This fine-scale heterogeneity could create population refugia during adverse conditions not represented in the current framework.
The model represents development as smooth, temperature-dependent transitions between life stages. In reality, metamorphosis involves complex physiological reorganisation that may be disrupted by environmental stressors. Nutritional stress during larval development can affect adult body size, longevity, and fecundity in ways more complex than simple linear relationships. Similarly, the model assumes successful development given adequate thermal conditions, missing potential failures during critical developmental windows.
While basic background mortality is included, the model excludes explicit representation of pathogen dynamics. Viral pathogens associated with other pollinators, such as black queen cell virus, sacbrood virus, and deformed wing virus, have been detected in Eristalis hoverflies (
The model represents individuals as identical except for stochastic variation in development timing. Real populations exhibit substantial variation in body size, metabolic rates, behavioural tendencies, and stress tolerance that could influence population resilience. By standardising individuals, the model may miss emergent properties arising from population heterogeneity, such as differential survival of stress-tolerant phenotypes during adverse conditions.
Thermal performance curves imply predictable development given environmental conditions. However, development rates exhibit substantial individual variation even under identical conditions, and environmental fluctuations may have non-linear effects on developmental outcomes. The model’s deterministic approach may underestimate population variability and resilience mechanisms that arise from developmental asynchrony.
The grid-based landscape representation treats space as discrete cells with defined boundaries. Hoverfly movement likely occurs along continuous gradients of resource quality and environmental conditions. This discretisation may create artificial barriers to movement or miss important edge effects where landscape elements meet. Additionally, the model assumes individuals can accurately perceive resource quality within their detection radius, potentially overestimating the efficiency of resource location.
The model assumes that multiple stressors (temperature, humidity, pesticides, resource limitation) combine in predictable, largely additive ways. However, synergistic interactions are common in biological systems, where the combined effect of multiple stressors exceeds the sum of individual effects. For example, temperature stress might increase pesticide susceptibility, or resource limitation might reduce detoxification capacity, creating non-linear responses to environmental challenges.
These simplifications reflect deliberate choices, balancing biological realism against parameter availability and computational feasibility. The extensive use of allometric scaling and cross-species parameter estimation highlights data limitations for this ecologically important but understudied species. Many key processes rely on assumptions derived from related species or theoretical considerations rather than empirical data specific to S. scripta.
For risk assessment applications, the model provides a framework for comparing relative risks across management scenarios rather than predicting absolute population outcomes. It is most valuable for identifying critical life stages vulnerable to pesticide exposure, evaluating how landscape composition influences population persistence, assessing the effectiveness of refuge areas in maintaining viable populations, and comparing the population-level consequences of different agricultural practices.
The model is less appropriate for predicting precise population abundances, assessing extinction probabilities in specific landscapes, evaluating long-term evolutionary responses to agricultural intensification, or extrapolating to hoverfly species with substantially different life histories (e.g., univoltine species, specialist predators, or non-migratory forms).
By acknowledging these boundaries explicitly, we position the model as a structured hypothesis about hoverfly population dynamics that can guide both risk assessment and future research priorities. The framework’s value lies not in perfect biological representation, but in providing a quantitative tool for exploring how environmental variability and management practices interact to influence pollinator and biocontrol services in agricultural landscapes.
We thank Francis Gilbert for sharing unpublished data and publications on S. scripta, Aleksandra Walczyńska for assistance with temperature-dependent development analyses of preimaginal stages, and two anonymous reviewers for their valuable comments and suggestions.
The authors have declared that no competing interests exist.
No ethical statement was reported.
No use of AI was reported.
This study was supported by the PollinERA project. PollinERA receives funding from the European Union’s Horizon Europe research and innovation Programme under grant agreement No.101135005. Views and opinions expressed are those of the author(s) only and do not necessarily reflect those of the European Union (EU) or the European Research Executive Agency (REA). Neither the EU nor REA can be held responsible for them.
Conceptualization: EZ, GS, XD, CJT. Formal analysis: EZ, XD. Funding acquisition: CJT. Investigation: EZ, GS. Supervision: CJT. Visualization: EZ. Writing - original draft: EZ, GS. Writing - review and editing: XD, CJT.
Elżbieta Ziółkowska https://orcid.org/0000-0002-7213-2200
Grzegorz Sowa https://orcid.org/0000-0001-7855-0545
Xiaodong Duan https://orcid.org/0000-0003-2345-4155
Christopher John Topping https://orcid.org/0000-0003-0874-7603
All of the data that support the findings of this study are available in the main text.