Introduction
⌅The
sesids or clear-wing moths (Lepidoptera: Sesiidae) are a striking
family of diurnal and heliophilous moths whose adults exhibit a marked
Batesian mimicry with the Hymenoptera, both in their appearance
(aposematic coloration often with yellow or red rings in the abdominal
segments, partly transparent wings with scaleless areas) and in their
behaviour (hovering flight). Adults of many species have functional
mouthparts and visit flowers during the daytime to feed on, although the
exact diel period of activity is often species-specific and
weather-sensitive. The larvae of sesids are phytophagous and
endophagous, with little pigmentation, usually with cream-white urites
and a brown head/prothoracic shield (Laštůvka & Laštůvka, 2001Laštůvka Z, Laštůvka A, 2001. The Sesiidae of Europe. Apollo Books, Stenstrup. 245 pp.
).
Several
clear-wing moths have specialised in woody host plants (xylophagous
species), often of closely related hosts (oligophagous species). Larvae
of these sesid species bore into the wood of the trunk, branches and/or
roots of their host trees and shrubs during larval development (1-4
years). Xylophagous sesids require living wood for their development,
even if some species prefer damaged, decayed, or diseased hosts (Pühringer, 1994Pühringer
F, 1994. Zur Biologie der oberösterreichischen Glasflügler
(Lepidoptera, Sesiidae). Entomol Arbeits Salzkammergut 1: 1–84.
).
Larvae develop under the host bark, boring irregular galleries in the
cambium zone and at the interface between dead and living tissues.
Larval galleries may be more or less grouped, even merged, with abundant
silk and reddish-brown frass that may be expelled to the outside.
Larval galleries are often associated with bark wounds and cracks,
thickened edges around debarked areas, bark previously altered by
mistletoe plants and other epiphytes, excrescences, tumescence, fungal
swellings, and bacterial cankers (Audemard & Vigouroux, 1982Audemard
H, Vigouroux A, 1982. Une curieuse association parasitaire sur Pêcher,
Sésie et tumeur bactérienne du collet. Phytoma Def Veg 337: 28–29.
; Pühringer, 1994Pühringer
F, 1994. Zur Biologie der oberösterreichischen Glasflügler
(Lepidoptera, Sesiidae). Entomol Arbeits Salzkammergut 1: 1–84.
). Xylophagous sesids can cause significant damage to their host plants (Fig. 1), so that some species are considered important pests of fruit and forest trees and shrubs (Allen, 1975Allen AA, 1975. Notes on a colony of Synanthedon vespiformis L. (Yellow-legged clearwing) in S.E. London (N.W. Kent) with special
reference to the breeding site. Entomol Rec J Var 87: 47–49.
; Laštůvka & Laštůvka, 2001Laštůvka Z, Laštůvka A, 2001. The Sesiidae of Europe. Apollo Books, Stenstrup. 245 pp.
).
In
recent years, damage by sesids to fagaceous trees has been reported in
different areas of Extremadura (SW Spain), specifically Synanthedon vespiformis (L.) in young chestnut plantations (Armendáriz et al., 2014Armendáriz J, Aza C, Bañuls P, Manzano M, Mateos J, 2014. Synanthedon vespiformis, un problema emergente en los castañares del norte de Cáceres. Phytoma España 255: 31–35.
) and in reforestations done in oak open woodlands (Del Moral et al., 2013Del Moral J, Casadomet E, Rebollo FJ, Moral FJ, Trigo E, Villafaina M, Villalba JA, 2013. Distribución de los daños de Synanthedon vespiformis en reforestaciones de encinas y alcornoques de la provincia de Badajoz.
I Congreso de la Dehesa y el Montado, Badajoz (España), November 6–7,
2013.
), although in many other cases the species
membership of the sesids causing damage was unknown. Evidence of the
poor knowledge of the clear-wing moths in the study region arises from
the preliminary results of this study, which has provided the first
provincial records of some sesid species associated with oaks (Montero-Calvo & Blázquez-Caselles, 2023Montero-Calvo
AJ, Blázquez-Caselles A, 2023. Sesiidae en Extremadura (España):
Revisión y nuevas citas (Insecta: Lepidoptera). Arquiv Entomol 26:
155–168.
; Torres-Vila & Montero-Calvo, 2024Torres-Vila
LM, Montero-Calvo A, 2024. Adenda a los sésidos (Lepidoptera: Sesiidae)
de Extremadura (SO España). Arquiv Entomol 28: 137–140.
).
Although sesid damage may occur in oaks of any age, the most severe
impact often occurs in young plants because the subcortical larval
galleries can gird and kill the host. Girdling can occur quickly with
crowded larval populations, but also due to damage accumulated over
years. Damage from sesids is widespread in oak reforestations and
densifications, where larvae can cause substantial mortality in young
trees in the first years after plantation. The objective of this study
was to determine the clear-wing moth species associated with oaks in the
region of Extremadura, as well as acquire knowledge on their chorology,
flight curves and diel activity.
Material and methods
⌅Study area
⌅This study covered all the region of Extremadura (SW Spain), which extends over 41,634 km2 and contains more than 1.2 million hectares of oak forests, most of
them open woodlands. The most important oak species are, in order of
importance, holm oak (Quercus ilex L.), cork oak (Quercus suber L.) and Pyrenean oak (Quercus pyrenaica Willd.). The climate is typically Mediterranean, with dry and warm
summers (up to 40 °C) and mild-rainy winters. The mean annual
temperature is close to 16 ºC (range 10-18 ºC) and the mean annual
precipitation is about 700 mm (range 360-1500 mm). Altitude ranges from
about 150 m (Guadiana and Tajo River valleys) to more than 2400 m
(Central System Mountain range), although the oak species rarely
populate areas above 1100-1200 m (holm and cork oaks) or 1500-1600 m
(Pyrenean oak) (Torres-Vila et al., 2019Torres-Vila
LM, Echave-Sanabria AC, Mendiola-Díaz FJ, Moral-García FJ, 2019.
Mapping oak shoot browning in SW Spain using online imagery as virtual
prospecting tool. Ann For Sci 76: 32. http://dx.doi.org/10.1007/s13595-019-0818-y
, 2023aTorres-Vila LM, Mendiola-Díaz FJ, Canelo T, 2023a. Cerambyx cerdo and Cerambyx welensii oak-living sympatric populations exhibit species-specific responses to face ecological factors in the wild. Diversity 15: 545. http://dx.doi.org/10.3390/d15040545
).
Chorology
⌅During
the spring (April-June) of two consecutive years (2021-2022), a
trapping network with synthetic sex pheromones was implemented
throughout the Extremadura region (Fig. 2).
This main sampling protocol was complemented with additional data
obtained during the years 2020 and 2023. In total, information was
collected from 38 sites, some of which were sampled for more than a year
(42 site/year combinations) (Supplementary Table S1).
Sampling sites were established mainly in reforestations and
densifications of holm and cork oak, but also of Pyrenean oak. In each
selected sampling site, standard delta traps were installed and baited
with commercial sex pheromones (OpenNatur®, manufacturer: Pherobank BV, The Netherlands) of each of the six oak-living sesid species reported in Iberia (De Freina & Witt, 1997De
Freina JJ, Witt TJ, 1997. Die Bombyces und Sphinges der
Westpalaearktis: Sesioidea: Sesiidae, Vol 4. Forschung &
Wissenschaft, Munich. 432 pp.
; Laštůvka & Laštůvka, 2001Laštůvka Z, Laštůvka A, 2001. The Sesiidae of Europe. Apollo Books, Stenstrup. 245 pp.
), namely Paranthrene insolita Le Cerf, 1914 [= P. insolitus]; Synanthedon stomoxiformis (Hübner, 1790); Synanthedon conopiformis (Esper, [1782]); Synanthedon codeti (Oberthür, 1881); Synanthedon vespiformis (L., 1761); and Synanthedon spuleri (Fuchs, 1908). We included S. stomoxiformis among the target species because it was mentioned in oaks by De Freina & Witt (1997) based on early observations by Staudinger (1879: 303)Staudinger O, 1879. Lepidopteren-Fauna Kleinasien´s. Horae Soc Ent Ross 14(1878): 176–482.
: “I suspect that Ses.[ia] stomoxyformis [sic] will live in oak trees, as I know it has been caught on oak trees
more often”. However, the available evidence suggests that it is rather
unlikely that this clear-wing moth uses oaks as host trees. The six
studied species have a western Palearctic distribution (Laštůvka & Laštůvka, 2001Laštůvka Z, Laštůvka A, 2001. The Sesiidae of Europe. Apollo Books, Stenstrup. 245 pp.
).
Flight curves
⌅In
several sites and years (n = 7 combinations) moth flight was monitored
with pheromone traps throughout the entire favourable season
(April-November) to build the flight curves of the target species
(site/year codes: 0, 22S, 31, 32, 33, 43S and 46F; Suppl. Table S1).
Pheromone diffusers were replaced every 30-40 days following the
manufacturer's instructions. Pheromone traps were inspected weekly,
changing each sticky plate for a new one and taking the sticky plates
with the catches to the laboratory for examination. The species
membership of all captured adults was verified based on their external
morphology (wing, thoracic and abdominal coloration patterns) under a
stereomicroscope. In case of doubt or poor preservation, the adults were
removed from the sticky plates to study their genitalia, diluting the
glue with a drop of hexane. The taxonomy was performed according to the
keys of Laštůvka & Laštůvka (2001)Laštůvka Z, Laštůvka A, 2001. The Sesiidae of Europe. Apollo Books, Stenstrup. 245 pp.
. From the catch data (Suppl. Table S1),
both abundance (mean catch number per trap per site per season in the
subset of traps with at least one capture) and occupancy (percentage of
traps with at least one capture) were estimated (Gaston et al., 2000Gaston
KJ, Blackburn TM, Greenwood JJ, Gregory RD, Quinn RM, Lawton JH, 2000.
Abundance-occupancy relationships. J Appl Ecol 37: 39–59. https://doi.org/10.1046/j.1365-2664.2000.00485.x
; Torres-Vila et al., 2022Torres-Vila
LM, Mendiola-Díaz FJ, Moral-García FJ, Canelo T, 2022. Large-scale
geostatistical mapping and occupancy-abundance patterns of Cerambyx species threatening SW Spain oak forests. Eur J For Res 141: 1045–1057. http://dx.doi.org/10.1007/s10342-022-01487-z
).
The observation of numerous specimens of S. vespiformis on the sticky plates suggested that adults captured in spring were larger than those captured in other seasons of the year, so we studied the effect of season and year on moth size. To do this, we measured the imaged males (see phototraps below) in Montánchez during 2022-2023 (site/year codes: 44F and 46F; Suppl. Table S1) using the forewing length (base-apex) as an estimator of body size. Only imaged males with at least one wing in horizontal position were measured. The sticky plate grid was used as a scale. Sample sizes ranged 14-71 individuals per season per year (total sample size n = 192). Wing measurements were done with EclipseNet 1.20 software using a Nikon DS-U1 digital camera mounted on a Leica S6D stereomicroscope.
Diel activity
⌅The diel activity of the most abundant sesid species (P. insolita, S. conopiformis and S. vespiformis) was investigated with automated traps baited with sex pheromones placed in two sites for two years (site/year codes: 22S, 43S, 44F and 46F; Suppl. Table S1). We used two types of automated traps that allowed us to know the time of adult capture by different methods.
First, we used a phototrap adapted from the PT2 trap model previously used with Cerambyx longhorn beetles (Torres-Vila et al., 2023bTorres-Vila
LM, Mendiola-Díaz FJ, López-Calvo R, Ponce-Escudero F, Sánchez-González
Á, Fernández-Moreno F, 2023b. Ad-hoc devised phototraps unravel Cerambyx miles diel activity in the wild (Coleoptera: Cerambycidae). Frag Entomol 55: 101–116.
).
The phototrap is formed by an image capture device (ICD) placed on the
top of a standard delta trap sticky plate baited with the sex pheromone
of the target species (Fig. 3A, 3B).
The ICD consists of 1) a central processing unit (Raspberry Pi mod. A+)
managed with Raspberry Pi OS v. 1.4 (formerly Raspbian); 2) a visible
light camera (Raspberry Pi Camera Module v. 2.0); 3) a quartz clock
installed in the Raspberry Pi GPIOs; and 4) a micro-SD port with a 32 Gb
memory card for the operating system and image storage. ICD electronic
components were arranged inside a watertight box (11 x 11 x 6 cm) and
powered by portable solar panels. The device was equipped with four
light-emitting diodes (LEDs) facing the image capture area (the entire
sticky plate) to enable imaging at twilight and night. The LEDs turned
on 5 seconds before each shot, enabling the digital camera to set
optimal sensitivity and exposure time, and they were shut off once the
shot was taken. The ICD script was set to take an image every 10
minutes. The phototrap setting was finished by placing some wooden
skewers or a piece of wire mesh on the ICD top to keep birds from
perching. A curved acetate sheet placed on top of the sticky plate
greatly increased trap effectiveness since moths entered easily through
the lateral apertures, but they crashed while in flight into the inner
acetate wall to fall on the glue (Fig. 3B). Images were viewed using Irfan View® free software, and image metadata (date, hour, site) were recorded for
each male moth captured. Images allowed a correct specific
identification in nearly all cases (> 99%), but in cases of doubt,
the species membership of the imaged adults was verified by examining
the adults glued to the sticky plates brought from the field.
Second, we used an infrared-sensor trap (Montero-Calvo, 2021Montero-Calvo
AJ, 2021. Sistema de monitorización remota de trampas Funnel para la
captura de heteróceros. Master thesis. UNED, Madrid.
)
formed by an infrared light-emitting device enclosed in a standard
funnel trap (covered with a small plastic roof to prevent rainwater from
entering) baited with the sex pheromone of the target species (Fig. 3C).
The device consists of a pass sensor with five infrared emitters and
paired receivers sensitive to the 940 nm wavelength, a NSL-19m51
brightness sensor, a Heltec WiFi LoRa 32 v2.1 board with an ESP32
microprocessor and a LoRa transceiver (Fig. 3D)
managed with a custom firmware. The components were powered by two
lithium-ion batteries integrated into the mother board. The infrared
barrier is always active, but when an insect passes through to enter the
trap, the barrier deactivates and wakes up the microprocessor, which
sends a capture event signal to a server via a LoRaWAN network. Once the
server confirms the reception, the device reactivates the infrared
barrier and goes back to sleep. The species membership of each capture
event was verified weekly by examining the adults captured in the funnel
trap container.
The automated traps were set, depending on trap type and site features, either on metal supports nailed to the ground, suspended from an oak branch, or fixed to the oak trunks at about 1.40-1.50 m height, as vertically as possible. Automated traps were usually inspected once a week to recover data and do maintenance operations. The number of catches in each trap was scored into 24 one-hour periods, and frequencies per hourly intervals were calculated prior to statistical analysis. Data from different sites, years and traps were pooled within species to build more robust curves of diel activity (site/year codes: 22S, 43S, 44F and 46F; Table S1).
Data analysis
⌅The
two-sample Kolmogorov-Smirnov (KS) test was used to compare frequency
distributions of diel activity (hourly captures) between species (Sokal & Rohlf, 1995Sokal RR, Rohlf FJ, 1995. Biometry. Freeman and Co, New York. 887 pp.
). Since S. vespiformis moth size was not normally distributed after a preliminary Shapiro-Wilk
test, a generalised linear model (GLM) using the Poisson distribution
with log link was computed to assess the effects on moth size of season
and year (both with fixed effects) as explanatory variables. Season
factor was scored in three classes (spring: April-June; summer:
July-September; autumn: October-November) and year factor in two classes
(2022 and 2023). Model error was tested for over- and under-dispersion,
and the residual plot was checked to verify the assumptions of the
fitted model. Analysis of deviance (Type II Wilks’ likelihood-ratio test
[LR Chi2]) was used to assess the effects of season, year
and their interaction on moth size. A post hoc Tukey contrast (|z|
values) was completed for multiple comparisons of means to establish
homogeneous groups among seasons. All statistics were computed with R
4.3.2 (R Core Team, 2023R Core Team, 2023. R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna. https://www.R-project.org/
).
Results
⌅Chorology
⌅Four of the six target species, P. insolita, S. vespiformis, S. codeti and S. conopiformis were well distributed throughout the study region, occurring in the three sampled forest habitats (holm, cork, and Pyrenean oak) and occupying a considerable altitudinal range (Fig. 2, Suppl. Table S1). On the contrary, S. stomoxiformis and S. spuleri were never captured. The total number of catches per species, as well as the species-specific values of abundance and occupancy, differed noticeably among species (Fig. 4). S. conopiformis was the most abundant species, but the moth with the highest occupancy was P. insolita, despite its relatively low abundance (Fig. 4). Note, however, that S. vespiformis autumn flight (see below) is not included in these statistics since trapping protocol only covered the spring (April-June). It follows that S. vespiformis abundance values are underestimated if the entire year is considered rather than just the spring period.
The commercial sex pheromones used showed a
good level of specificity. Even so, there was cross-attraction with
three non-target sesids (not associated with oaks) that were captured in
the traps (Suppl. Table S1, Fig. 4), in order of abundance: Bembecia uroceriformis (Treitschke, 1834), Pyropteron chrysidiformis (Esper, 1782) and Pyropteron (Synansphecia) leucomelaena (Zeller, 1847). The occupancy of these three non-target species did not exceed 20% in any case (Fig. 4). It is important to note that the S. conopiformis sex pheromone was extremely attractive to B. uroceriformis; in fact, all B. uroceriformis specimens were captured in traps baited with S. conopiformis pheromone (see Pühringer, 1996Pühringer F, 1996. Utilities zum Pheromonfang von Sesien (Lepidoptera, Sesiidae). Entomol Nachr 3: 8–12.
).
Flight curves
⌅The flight curves showed that P. insolita (Fig. 5A) and S. conopiformis (Fig. 5B) exhibit spring activity (April-June), with flight peak dates that may vary up to almost a month depending on the site and year. The data available for S. codeti were more modest but clearly indicate that its flight period is longer and later (May-October) than in the two preceding species, with a marked summer peak (July) (Fig. 5C). In the case of S. vespiformis, adult activity covered the longest seasonal period (early April to early November), with two flight peaks in May and September-October (Fig. 5D).
Moth size in S. vespiformis was not normally distributed (Shapiro-Wilk test, W = 0.98, P < 0.01). Moth size was significantly affected by the season (Analysis of deviance, LR Chi2 = 16.61, df = 2, P < 0.001) but not by the year (LR Chi2 = 0.51, df = 1, P = 0.48), with no season × year interaction (LR Chi2 = 0.06, df = 2, P = 0.97) (Fig. 6). So, we pooled both years and re-analysed the data with the season as the only explanatory variable (LR Chi2 = 16.40, df = 2, P < 0.001). A post hoc of this model showed that S. vespiformis moths were significantly larger in spring than in either summer (|z| = 3.73, P < 0.001) or autumn (|z| = 3.01, P < 0.01), with no significant differences between the summer and autumn seasons (|z| = 0.05, P = 0.99) (Fig. 6).
Diel activity
⌅Diel activity was notably different between the three target species for which data were available: P. insolita, S. vespiformis and S. conopiformis (Fig. 7). Although the three species were active from early afternoon until late evening (from about 14:00 to 22:30 h), the earliest flight peak was that of P. insolita (15:00-18:00 h), followed by S. vespiformis (17:00-19:00 h), and then by S. conopiformis (19:00-21:00 h) (Fig. 7). Diel activity was significantly earlier in S. vespiformis than in S. conopiformis (KS test, D-stat = 0.642 > D-crit = 0.110, P < 0.001). KS tests were not computed with P. insolita due to the low sample size recorded for this species in automated traps. Distinctly enough, the diel activity of B. uroceriformis (a non-target sesid species) took place in the morning, with a relatively early flight peak (9:00-11:00 h) (Fig. 7) (all local time, GMT+2).
Discussion
⌅Abundance and occupancy values show overall that the most frequent sesid species associated with oaks in Extremadura are S. conopiformis and S. vespiformis, followed at some distance by P. insolita and S. codeti,
although in the case of the last species, more information would be
useful to better ascertain its actual impact on oaks. The presence of S. stomoxiformis was not detected despite having been reported from relatively close Spanish provinces and Portuguese districts (Laštůvka & Laštůvka, 2014Laštůvka
Z, Laštůvka A, 2014. Sesiidae of the Iberian Peninsula, new records and
distributional analysis (Insecta: Lepidoptera). SHILAP Rev Lepid 42:
559–580.
; Álvarez et al., 2021Álvarez
M, Aguado LO, Noval N, Álvarez P, 2021. New data, updated distributions
and flower preferences of the clearwing moths (Lepidoptera, Cossoidea,
Sesiidae) of mainland Spain. Bol SEA 68: 289–305.
), possibly due to the more xeric conditions of most sampled habitats in Extremadura. The non-detection of S. spuleri was not surprising since this species is only known in Spain from the province of Lleida (Álvarez et al., 2021Álvarez
M, Aguado LO, Noval N, Álvarez P, 2021. New data, updated distributions
and flower preferences of the clearwing moths (Lepidoptera, Cossoidea,
Sesiidae) of mainland Spain. Bol SEA 68: 289–305.
).
Our occupancy estimates must be considered quite robust (including
particularly absence data) because it is highly unlikely that a
pheromone trap fails to detect a local population over a full flight
season, considering the high levels of detectability that sexual
pheromones provide, specifically in clear-wing moths (Burman et al., 2016Burman
J, Westerberg L, Ostrow S, Ryrholm N, Bergman KO, Winde I, Nyabuga FN,
Larsson M, Milberg P, 2016. Revealing hidden species distribution with
pheromones: the case of Synanthedon vespiformis (Lepidoptera: Sesiidae) in Sweden. J Insect Conserv 20: 11–21. http://dx.doi.org/10.1007/s10841-015-9835-9
).
Automated trap data showed that the diel
activity of the three species studied may extend from early afternoon to
late evening, but flight peaks were clearly different between species,
first P. insolita, then S. vespiformis and finally S. conopiformis,
which reveals that each species displays a preferred diel flight
period. Activity times were quite similar to those reported in central
Europe, despite the latitude difference (Pühringer, 1994Pühringer
F, 1994. Zur Biologie der oberösterreichischen Glasflügler
(Lepidoptera, Sesiidae). Entomol Arbeits Salzkammergut 1: 1–84.
, 1996Pühringer F, 1996. Utilities zum Pheromonfang von Sesien (Lepidoptera, Sesiidae). Entomol Nachr 3: 8–12.
; Szántóné-Veszelka et al., 2010Szántóné-Veszelka M, Poós B, Szőcs G, 2010. Blackberry and raspberry, new hosts of the yellow legged clear-wing moth, Synanthedon vespiformis:
what can the recently developed sex attractant offer in monitoring and
beyond? IOBC Working Group, Integrated Plant Protection in Fruit Crops
Subgroup “Soft Fruits”, 7th Workshop on Integrated Soft Fruit
Production, pp: 20–23.
). In the case of P. insolita, diel activity was similar to that reported in Turkey and other Spanish regions, irrespective of the subspecies considered (Spatenka & Laštůvka, 1997Spatenka K, Laštůvka Z, 1997. Zur Verbreitung und Variabilität von Paranthrene insolita Le Cerf, 1914 (Lepidoptera, Sesiidae). Nachr Entomol Ver Apollo NF 18: 13–21.
).
Seasonal flight curves were considerably different between species. Adult activity of P. insolita and S. conopiformis was in spring, that of S. codeti was in summer, and distinctly S. vespiformis activity extended over a long period from spring to autumn, as previously reported (Levi-Zada et al., 2011Levi-Zada
A, Ben-Yehuda S, Dunkelblum E, Gindin G, Fefer D, Protasov A,
Kuznetsowa T, Manulis-Sasson S, Mendel Z, 2011. Identification and field
bioassays of the sex pheromone of the yellow-legged clearwing Synanthedon vespiformis (Lepidoptera: Sesiidae). Chemoecology 21: 227–233. http://dx.doi.org/10.1007/s00049-011-0081-7
; Armendáriz et al., 2014Armendáriz J, Aza C, Bañuls P, Manzano M, Mateos J, 2014. Synanthedon vespiformis, un problema emergente en los castañares del norte de Cáceres. Phytoma España 255: 31–35.
). However, flight curves recorded in Extremadura differed ostensibly from the phenology reported in the Pühringer’s (2024)Pühringer F, 2024. Phenology of Palearctic clear wing moths (Lepidoptera: Sesiidae). https://www.sesiidae.net/phenology.htm [2 May 2024].
database: in Extremadura, P. insolita and S. conopiformis showed earlier activity (roughly a month); S. codeti showed later activity (about a month), while S. vespiformis showed a much longer activity period, especially at the end of the season (from early April to mid-November).
The case of S. vespiformis deserves special attention. Captures as late as those observed in this
study (until mid-November) had never been reported before to our
knowledge. Furthermore, flight curves in Montánchez showed for two years
a marked bimodal pattern, with well-differentiated maxima in spring and
autumn and minimal (or non-existent) moth population during the summer.
In other sites/years, the bimodal pattern of S. vespiformis was
less evident, likely due to a lower number of trap catches. A bimodal
flight pattern, although less pronounced, has also been reported in
Extremadura in a previous study (Armendáriz et al., 2014Armendáriz J, Aza C, Bañuls P, Manzano M, Mateos J, 2014. Synanthedon vespiformis, un problema emergente en los castañares del norte de Cáceres. Phytoma España 255: 31–35.
). Further field research is needed to determine whether the bimodal flight pattern of S. vespiformis reported here is widespread in southern Iberia or just occurs locally
due to unknown ecological and meteorological factors. In any case, the
bimodal flight pattern does not fit with the presence data reported in
central European countries, where S. vespiformis either displays a more-or-less continuous flight through the season (Szántóné-Veszelka et al., 2010Szántóné-Veszelka M, Poós B, Szőcs G, 2010. Blackberry and raspberry, new hosts of the yellow legged clear-wing moth, Synanthedon vespiformis:
what can the recently developed sex attractant offer in monitoring and
beyond? IOBC Working Group, Integrated Plant Protection in Fruit Crops
Subgroup “Soft Fruits”, 7th Workshop on Integrated Soft Fruit
Production, pp: 20–23.
; Schmitt et al., 2021Schmitt
J, Bartsch D, Markl G, 2021. Verbreitung, Habitatnutzung und Phänologie
der Glasflügler im Raum Tübingen (Lepidoptera: Sesiidae). Carolinea 79:
83–112. https://doi.org/10.57962/regionalia-20315
) or maximum catches in June-July (Pühringer, 2024Pühringer F, 2024. Phenology of Palearctic clear wing moths (Lepidoptera: Sesiidae). https://www.sesiidae.net/phenology.htm [2 May 2024].
), precisely when moth populations are low or absent in our study area.
The bimodal flight pattern of S. vespiformis detected in Extremadura should not be mistakenly interpreted as a
bivoltine one, i.e., the result of two annual larval generations.
Although it has been suggested that S. vespiformis may have more than one generation (Armendáriz et al., 2014Armendáriz J, Aza C, Bañuls P, Manzano M, Mateos J, 2014. Synanthedon vespiformis, un problema emergente en los castañares del norte de Cáceres. Phytoma España 255: 31–35.
),
the occurrence of two or more generations per year has never been
proven in a xylophagous sesid species to our knowledge. Woodborers in
general, and sesids in particular, show a rather slow development due to
the low nutritional quality of the wood. So, it is unlikely that in
just about six months (May-October) the offspring of spring adults will
complete their life cycle to produce the autumn flight (see Pühringer, 1994Pühringer
F, 1994. Zur Biologie der oberösterreichischen Glasflügler
(Lepidoptera, Sesiidae). Entomol Arbeits Salzkammergut 1: 1–84.
). Whether autumn adults were the progeny of spring adults, this would also imply that S. vespiformis does not exhibit obligate diapause. Even less likely would be that the
offspring of the autumn flight could complete their development under
winter cold conditions to emerge in the next spring. Moreover, S. vespiformis larvae likely stop their development and overwinter. Finally, the fresh
appearance and absence of desquamation of the adults captured in early
autumn suggest their recent emergence from the pupa, which would rule
out that they are spring adults experiencing aestivation.
The bimodal flight distribution of S. vespiformis is likely to be the result of a single generation, but with two
well-differentiated periods of adult emergence. It has been suggested
that spring rainfall (early March) and summer storms (late July-early
August) could be used as cues by S. vespiformis to initiate the spring and autumn emergence periods, respectively (Crégu, 2019Crégu
A, 2019. Ecologie et chorologie d’une famille de lépidoptères méconnue,
les Sesiidae. Mémoire Diplôme de l’École Pratique des Hautes Études,
MNHN-PSL Research University, Paris. 107 pp.
). On the
contrary, it has also been speculated that bimodal flight could result
from low flight activity in the early summer rainy period (Schmitt et al., 2021Schmitt
J, Bartsch D, Markl G, 2021. Verbreitung, Habitatnutzung und Phänologie
der Glasflügler im Raum Tübingen (Lepidoptera: Sesiidae). Carolinea 79:
83–112. https://doi.org/10.57962/regionalia-20315
). In any case, available evidence suggests that a part of the S. vespiformis population uses the strategy of flying in spring and the rest in
autumn. The bimodal pattern could be adaptive if it evolves to avoid
extreme summer conditions of heat and drought, which are increasingly
frequent in SW Spain under the current climate change scenario. The
smaller body sizes of summer and autumn adults than spring adults agree
with this idea, since it suggests that the larvae of both groups have
endured different thermal conditions during their development. The
smaller size of the summer and autumn adults could derive from the fact
that larvae completed the final stages of development in the hot season,
as larval growth speed in insects increases with temperature at the
cost of producing smaller adults (Torres-Vila, 1996Torres-Vila
LM, 1996. Efecto de la temperatura de desarrollo preimaginal sobre el
potencial biótico de la polilla del racimo de la vid, Lobesia botrana (Denis y Schiffermüller, [1775]) (Lepidoptera: Tortricidae). SHILAP Rev Lepid 24: 197–206.
; Angilletta et al., 2004Angilletta
MJ, Steury TD, Sears MW, 2004. Temperature, growth rate, and body size
in ectotherms: fitting pieces of a life-history puzzle. Integr Comp,
Biol 44: 498–509. http://dx.doi.org/10.1093/icb/44.6.498
; Kingsolver & Huey, 2008Kingsolver J, Huey R, 2008. Size, temperature, and fitness: three rules. Evol Ecol Res 10: 251–268.
).
Tree physiology-mediated seasonal differences in the quality of food
available to larvae could also be involved in the adult size variation
observed. Consistent with these ideas, small and large S. vespiformis larvae can be found at the same time in the same host, although they can reach adulthood the same year (FES, 2024FES [Flemish Entomological Society], 2024. Catalogue of the Lepidoptera of Belgium, Synanthedon vespiformis (Linnaeus, 1761). https://projects.biodiversity.be/lepidoptera/species/4920/ [24 April 2024].
).
The bimodal flight pattern of S. vespiformis also poses an interesting ecological and evolutionary scenario. In the
absence of gene flow between the spring and autumn moth phenotypes,
life-history theory predicts that the temporal segregation of both
phenotypes should promote a speciation process. Drivers that could act
against speciation by allowing gene flow between both seasonal
phenotypes are the few summer adults (serving as a “bridge” between
spring and autumn) and the larval development of more than a year in a
fraction of the population (FES, 2024FES [Flemish Entomological Society], 2024. Catalogue of the Lepidoptera of Belgium, Synanthedon vespiformis (Linnaeus, 1761). https://projects.biodiversity.be/lepidoptera/species/4920/ [24 April 2024].
) whose emergence period could putatively occur in spring or summer. It follows that the life cycle of S. vespiformis in SW Iberia deserves additional study.
In conclusion, our research contributes to a better knowledge of the chorology, phenology, ecology and behaviour of the main clear-wing moth species associated with oaks in SW Spain, P. insolita, S. conopiformis, S. codeti and S. vespiformis. This information will be useful to improve integrated pest management methods given the increasing phytosanitary impact of these woodborers on oak open forests in Extremadura and other Iberian regions.
Supplementary material
⌅(Table S1) accompanies the paper on Forest Systems’ website.
Data availability
⌅Additional data beyond those already provided in this paper will be made available on reasonable request to the first author.
Acknowledgements
⌅This research was supported by the Servicio de Sanidad Vegetal (SSV, Junta de Extremadura) and the Centro de Investigaciones Científicas y Tecnológicas de Extremadura (CICYTEX, Junta de Extremadura). Partial financial support was received from the European Regional Development Fund (ERDF) through the GR18057 research group.
Competing interests
⌅The authors have declared that no competing interests exist.
Authors’ contributions
⌅Luis M. Torres-Vila: Conceptualization, Formal analysis, Investigation, Methodology, Resources, Supervision, Writing - original draft, Writing - review & editing. Adrián J. Montero-Calvo: Conceptualization, Investigation, Methodology, Resources, Software, Supervision, Writing - review & editing. Javier Mendiola-Díaz: Investigation, Methodology, Writing - review & editing. Rafael López-Calvo: Conceptualization, Investigation, Methodology, Software, Writing - review & editing. Álvaro Sánchez-González: Investigation, Methodology, Writing - review & editing. Francisco Ponce-Escudero: Investigation, Methodology, Writing - review & editing. Félix Fernández-Moreno: Investigation, Methodology. Zdeněk Laštůvka: Conceptualization, Investigation, Methodology, Writing - review & editing.
Funding
⌅| Funding agencies/institutions | Project / Grant |
|---|---|
| European Regional Development Fund (ERDF) | GR18057 research group |