Abstract
18
The spotted-wing drosophila ( Drosophila suzukii), a highly invasive agricultural pest, poses 19
significant challenges to fruit production worldwide. Traditional chemical control methods are 20
costly and raise concerns about resistance and environmental sustainability. The Heterospecific 21
Sterile Insect Technique (h-SIT) has emerged as a promising alternative, using sterile heterospecific 22
males (Drosophila melanogaster ) to suppress D. suzukii populations through reproductive 23
interference. However, optimizing irradiation doses is critical to balancing male sterility, 24
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maintaining biological quality and mating performances. This study aimed to determine the optimal 25
irradiation dose for D. melanogaster males by assessing their sterility, longevity, and courtship 26
behavior following exposure to gamma-ray doses ranging from 80 to 180 Gy. Results showed a 27
significant reduction in fertility across all irradiation doses, with near-complete sterility at 180 Gy. 28
However, longevity decreased with increasing doses, with males irradiated at 160–180 Gy showing 29
a lifespan reduction of up to 50 days compared to controls. Behavioral trials revealed that irradiated 30
D. melanogaster males retained their courtship ability toward D. suzukii females, although males 31
exposed to 160 Gy exhibited reduced courtship activity. These findings highlight that, among the 32
tested doses, 80 Gy emerged as the most effective, preserving male longevity and mating 33
performance while significantly reducing fertility. While 180 Gy achieved the highest sterility, the 34
potential lifespan and courtship behavior trade-offs warrant further evaluation. Future studies 35
should evaluate field performance to refine the balance between sterility, longevity, and mating 36
performances for effective D. suzukii population suppression. 37
38
1. Introduction 39
The spotted-wing drosophila (SWD), Drosophila suzukii (Matsumura) (Diptera: Drosophilidae) is 40
an invasive agricultural pest native to Southeast Asia (1). Since its first detection in California in 41
2008, D. suzukii has rapidly expanded its geographical distribution in many other states of United 42
States and across the globe, becoming a severe agricultural pest also in Europe, South America, and 43
parts of Africa (2–4). According to recent studies, the economic damage caused by D. suzukii in the 44
United States alone reaches hundreds of millions of US dollars annually, and in Europe, similar 45
losses are reported, suffering significant economic damage in their fruit industries (5,6). The rapid 46
spread of D. suzukii has been facilitated by its exceptional ability to thrive in diverse environmental 47
conditions, facilitated by its broad temperature tolerance and adaptability to different habitats (1,7). 48
One of the factors contributing to the invasive success of D. suzukii is its nutritional versatility. D. 49
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suzukii can attack a broad range of ripening fruits, including soft-skinned berries and stone fruits 50
with economic relevance; then, larval development causes fruit to rot rapidly due to the introduction 51
of rot-type pathogens at the oviposition site (8). 52
To counter the negative impact of D. suzukii, efficient and prompt population control actions are 53
required. Chemical insecticides, especially organophosphates, pyrethroids and spinosyns, were the 54
first and most effective control approach, but this strategy presents multiple challenges (9,10). 55
Insecticides must be applied several times per growing season, due to D. suzukii short generation 56
time and larval development inside the fruits (6,9). Thus, repeated exposure, short generation time, 57
and high fecundity have led to metabolic and penetration resistance development to spynosyns and 58
pyrethroids, raising concerns about the environmental sustainability of this approach (11,12). 59
Alternatively, significant research has been devoted to finding sustainable control measures under 60
an Integrated Pest Management approach (13–16). 61
In recent years, there has been a renewed interest in the use of SIT (Sterile Insect Technique) 62
and the release of sterile heterospecific males (i.e., heterospecific-Sterile Insect Technique) for pest 63
control (17–20). Both approaches can be developed under similar theoretical frameworks. SIT 64
consists in releasing large numbers of sterile males of the target pest species into the environment to 65
mate with conspecific wild females. The unfertile mating between the released sterile males and 66
wild females leads to a gradual decline in the pest population over time (21,22). Contrary to the 67
SIT, in heterospecific SIT, sterile males from closely related species are released to compete with 68
the pest population for mates. The heterospecific SIT leverages reproductive interference, a 69
reproductive interaction between individuals of different animal co-generic species and/or 70
subspecies, which results in fitness costs for one or both the interacting individuals (23–27). It 71
Results
from incomplete mating barriers between species and can occur at any stage of mate 72
acquisition through different mechanisms, from courtship to mating (24,25,27). 73
The irradiation dose is a key factor for the successful implementation of these approaches, 74
requiring a careful balance between achieving sufficient male sterility and preserving the biological 75
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performance of irradiated individuals. Studies on the evaluation of irradiation dose effects on 76
different insect pests (e.g., Ceratitis capitata Wiedemann, Anopheles arabiensis Patton, Aedes 77
aegypti L., Aedes albopictus Skuse) highlighted that an optimal irradiation dose can induce full 78
sterility without significantly compromising the biological qualities of males (28–32). At the same 79
time, improperly calibrated irradiation can lead to males that either retain some level of fertility or 80
exhibit impaired mate-finding abilities (29,30), emphasizing the necessity of refining the irradiation 81
dose to balance sterility and biological fitness. 82
Our previous studies demonstrated that Drosophila melanogaster (Meigen) could be a good 83
candidate for D. suzukii’s control species into a heterospecific SIT context. The two species have 84
incomplete pre-mating and complete post-mating isolation, and reproductive interference has been 85
documented between them (19). Furthermore, under laboratory conditions, D. melanogaster males 86
irradiated at 60 and 80 Gy were able to court and mate with D. suzukii females, leading to a 87
significant offspring reduction, although residual fertility has been observed in irradiated males 88
(20). These results provided the first foundation to develop heterospecific SIT against D. suzukii. 89
The aim of this study was to detect the optimal irradiation dose. First, we investigated the effect 90
of 6 different doses from 80 to 180 Gy on the sterility of D. melanogaster males and assessed their 91
fertility, through mating trials with D. melanogaster females. Second, we investigated the effect of 92
the irradiation on male longevity. Finally, we studied the courtship behavior of irradiated D. 93
melanogaster males analyzing the time spent courting D. suzukii females in relation to the different 94
irradiation doses administered. 95
96
2. Materials and Methods 97
2.1. Fruit fly colonies and rearing techniques 98
Drosophila suzukii and D. melanogaster used in this study were reared at the Sapienza University 99
of Rome facilities. The colonies are maintained in the BugDorm-4H4545 insect cages (47.5 x 47.5 x 100
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47.5 cm) in a thermostatic chamber at 25 ± 1°C, with a 14:10 hour light-dark cycle and with a 101
humidity of 70%. The insects were fed with food substrate based on corn flour (84.1% water, 0.7% 102
agar, 3.2% table sugar, 3.6% yeast, 7.2% corn flour, 1.0% soy flour, 0.2% methylparaben dissolved 103
in 25 mL of 70% ethanol) (33). Each week, the substrate was replaced with a fresh one to allow the 104
insects to feed and lay eggs. The previous substrate was labeled and placed in specified containers 105
to allow the development of new individuals within the colony. The colonies had unrestricted 106
access to water due to cotton balls soaked in a sugar-water solution (1:10 ratio), placed on top of the 107
cages. 108
109
2.2. Drosophila melanogaster males’ sterilization and individuals’ 110
selection 111
Sterilization of D. melanogaster males was performed at the Calliope gamma irradiation facility at 112
the ENEA Casaccia Research Center (Rome) at different total absorbed doses with a dose rate value 113
of about 130 Gy/h. The Calliope is a pool-type facility equipped with n.25 60Co radioisotope 114
sources (mean energy 1.25 MeV) in a high volume (7.0 x 6.0 x 3.9 m) shielded cell (34). Males to 115
be sterilized were chosen by checking their emergence from mature pupae into breeding falcons 116
every 30 minutes. In this way, newly emerged males of both species were collected and isolated 117
from females as soon as they were born, avoiding unwanted mating before the experiment. The 118
virgin males collected were placed in separate cages by species, and after 72-96 hours, they were 119
taken to the irradiation center for sterilization. 120
121
2.3. Irradiation effect on D. melanogaster male’ sterility 122
To evaluate the degree of sterility achieved by D. melanogaster males after irradiation, we 123
performed mating experiments between irradiated D. melanogaster males and fertile D. 124
melanogaster females. Seven treatments were set up, the control using non-irradiated individuals, 125
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and six treatments relating to the following irradiation doses: 80 Gy, 100 Gy, 120 Gy, 140 Gy, 160 126
Gy, and 180 Gy. D. melanogaster males were selected and irradiated as previously described. 127
Afterward, we placed five sterilized D. melanogaster males and five virgin D. melanogaster 128
females inside 50 ml falcon tubes containing food substrate; we adopted the same procedure for the 129
control individuals. We assessed the experiment in a thermostatic chamber at 25 ± 1°C, with a 130
14:10 hour light-dark cycle and with a humidity of 70%. After six days, we removed the adult 131
individuals and awaited the emergence of the newborns. We counted and noted newly emerged 132
adults daily. We performed five replicates for each condition. 133
134
2.4. Irradiation effect on D. melanogaster male’ longevity 135
To evaluate the effect of irradiation on the survival of D. melanogaster males, we compared the 136
average lifespan between irradiated and non-irradiated D. melanogaster males. We selected 72-96-137
hour-old D. melanogaster males that were irradiated as described in the previous paragraph at the 138
following doses: 80 Gy, 100 Gy, 120 Gy, 140 Gy, 160 Gy, 180 Gy. For each dose, we set up an 139
experimental cage (30 x 30 x 30 cm) with 20 individuals each. Two other cages were set up as 140
controls, in which we placed non-irradiated individuals: one cage was called “home control” with 141
individuals maintained at constant conditions of the thermostatic chamber, and one cage called “trip 142
control”, with individuals that we transported to the ENEA Calliope facility, but outside of the 143
irradiation unit. The “trip control” allowed us to evaluate if the transport could induce an impact on 144
the longevity of the individuals. For all conditions, we carried out mortality checks every day until 145
all the individuals died. 146
147
2.5. Irradiation effect on D. melanogaster male’ courtship behavior 148
We conducted courtship experiments to evaluate the time spent courting D. suzukii females by D. 149
suzukii and irradiated D. melanogaster males and to assess potential differences in the courtship 150
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time in relation to the administered irradiation doses. We selected individuals following the 151
Methods
of the previous analyses. In this experiment, we irradiated 72-96 hours old D. 152
melanogaster males only at 80 Gy, 160 Gy and 180 Gy. We did not consider irradiations at 100, 153
120, and 140 Gy because they did not lead to significant differences in terms of sterility and 154
longevity (see Results section). 155
We set up “no-choice” and “choice” experimental trials: in the “no-choice” condition, we 156
placed one D. suzukii female with homospecific or heterospecific male into a falcon (15 mL) and 157
analyzed the male courtship time. Specifically, we analyzed: - the courtship time of D. suzukii male 158
with a D. suzukii female; - the courtship time of D. melanogaster male irradiated at 80, 160 and 180 159
Gy with a D. suzukii female. In the “choice” conditions, we placed one D. suzukii female with two 160
homospecific or heterospecific males into a falcon (15 mL) to evaluate the male's courtship time. 161
Specifically, we analyzed: - the courtship time of two no-irradiated D. suzukii males with a D. 162
suzukii female; - the courtship time of one no-irradiated D. suzukii male and one D. melanogaster 163
male irradiated at 80, 160 and 180 Gy with a D. suzukii female. For the observation of behaviors 164
between two D. suzukii males, due to their morphological similarity, the videos were analyzed at 165
reduced playback speed to track the individuals and annotate their behaviors accurately. 166
Conversely, in the second condition involving heterospecific males, the two species were 167
distinguishable: D. suzukii males possess characteristic black spots on their wings (hence the name 168
"spotted-wing drosophila"), which are absent in D. melanogaster males. For all conditions, 169
following a 5-minute acclimation period, we recorded the individual's behavior for 10 minutes 170
using an Olympus Tough TG-6 camera. After recording, we analyzed the videos using the Boris 171
software (Behavioral Observation Research Interactive Software), taking into account the courtship 172
elements such as orientation, touch, wing scissoring, wing spreading, and copulation attempt 173
(35,36). We carried out 20 replications for each trial to ensure the robustness of our data. 174
175
2.6. Data analysis 176
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In the sterility experiment, the sterility degree achieved by D. melanogaster males was 177
evaluated for each experimental cond ition, applying a GLM model (generalized linear model with 178
negative binomial distribution), and the model family was selected comparing the AIC and BIC 179
estimators and the likelihood ratio test. We performed Tukey's multiple comparison test as a post 180
hoc test using the ‘multcomp’ package (37). The average percentage of residual fertility in each 181
condition was obtained by calculating the percentage reduction of each replicate in a specific 182
condition compared to the mean of offspring born in the control condition (i.e. 100% fertility) and 183
calculating the mean (± SE) of the percentages obtained in each replicate. 184
To evaluate the effect of the irradiation dose on the longevity of D. melanogaster males, 185
survival distributions of the different D. melanogaster groups (‘Control cages’, ‘Control trip’, ‘80 186
Gy’, ‘100 Gy’, ‘120 Gy’, ‘140 Gy’, ‘160 Gy’, ‘180 Gy’) were computed using the Kaplan-Meier 187
Method
with the ‘ survival’ package and the differences between survival distributions were 188
estimated using the Log-Rank Test with the ‘survminer’ package (38,39). 189
In the courtship experiment, to compare the courtship time of D. suzukii and D. melanogaster 190
males in “no-choice” condition, we used a GLM model (generalized linear model with negative 191
binomial distribution), selecting the model family based on the AIC and BIC estimators and the 192
likelihood ratio test. We performed Tukey's multiple comparison test as a post hoc test. In the 193
“choice” condition, we used a GLM model (generalized linear model with negative binomial 194
distribution) to compare the average courtship time of males. Then, we compared the average 195
courtship time of the two males in the same condition using the nonparametric statistical Wilcoxon 196
Signed Rank test using the ‘dplyr’ package (40). All analyses were carried out using R Software 197
version 3.6.2. (41). 198
199
3. Results 200
3.1. Drosophila melanogaster males’ sterilization 201
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We assessed the sterility of D. melanogaster males by mating them with D. melanogaster females 202
at irradiation doses of 80, 100, 120, 160, and 180 Gy, with a non-irradiated control group for 203
comparison. The mean number of the emerged adults in the control condition was 171.8 (± 24.47) 204
(mean ± SE) (Table 1). A significant emergence reduction was observed at all irradiation doses. At 205
the 80 Gy irradiation condition, the mean number of emerged adults was 29.2 (± 9.25), while at 206
180 Gy irradiation, it dropped to 0.8 (± 0.58) (Table 1; Fig 1). The GLM model showed a 207
significant effect of the male irradiation dose on the number of offspring produced by D. 208
melanogaster females (Table 2). Tukey's multiple comparison test showed a significant offspring 209
reduction from the control condition to all irradiation conditions, i.e. 80 Gy (z = 4.253, p = <0.001), 210
100 Gy (z = 5.183, p = <0.001), 120 Gy (z = 5.634, p = <0.001), 140 Gy (z = 6.660, p = <0.001), 211
160 Gy (z = 7.194, p = <0.001) and 180 Gy (z = 8.317, p = <0.001). There were also significant 212
differences between the 80 Gy irradiation dose and 160 Gy (z = 3.497, p= 0.008) and 180 Gy (z = 213
5.535, p= <0.001) doses. The 180 Gy dose showed significant differences with 80 Gy (see above), 214
100 Gy (z = -4.886, p= <0.001), 120 Gy (z = -4.559, p= <0.001) and 140 Gy (z = -3.761, p= 0.003) 215
doses, but not with 160 Gy. We did not observe significant differences between 80, 100, 120 and 216
140 Gy (Fig 1). 217
218
Table 1 . The mean number of the emerged D. melanogaster 219
adults. Mean number (±SE) of emerged adults and average 220
percentage (±SE) of the residual fertility at the different treatment 221
doses (Gy). 222
Treatment Dose (Gy)
Mean number of
emerged adults
(±SE)
Average percentage
(±SE) of residual
fertility
0 Gy 171.8 (± 24.47) 100 %
80 Gy 29.2 (± 9.25) 17 % (± 5.38)
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100 Gy 23.5 (± 5.52) 11.29 % (± 3.45)
120 Gy 19.5 (± 2.25) 9.19 % (± 2.38)
140 Gy 11.75 (± 2.66) 5.59 % (± 1.73)
160 Gy 5.25 (± 2.39) 3.05 % (± 24.47)
180 Gy 0.8 (± 0.58) 0.47 % (± 0.34)
223
224
Table 2. Irradiation effect on D. melanogaster male’ sterility. GLM model values are shown. 225
Values in boldface indicate significant differences. 226
Fixed Effects Estimate ±SE z Value p-Value
(Intercept) 2.9653 0.3051 9,718 < 2e-16
120 Gy -0.2053 0.4342 -0.473 0.63643
140 Gy -0.7035 0.4435 -1.586 0.11272
160 Gy -1.3070 0.4942 -2.645 0.00817
180 Gy -3.1884 0.6526 -4.886 1..03e-06
80 Gy 0.4089 0.4275 0.956 0.33882
No irradiation 2.1811 0.4208 5.183 2.18e-07
227
228
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229
Fig 1. Irradiation effect on D. melanogaster male’ sterility. The number of D. melanogaster adults 230
emerged from fertile females and irradiated males. Different letters mean significant differences by Tukey 231
Multiple Comparison tests (p < 0.05). 232
233
3.2. Irradiation effects on D. melanogaster male’s longevity 234
In the longevity tests of D. melanogaster males, Kaplan- Meier curves showed significant 235
differences in lifespan between the treatments (80 Gy, 100 Gy, 120 Gy, 140 Gy, 160 Gy, 180 Gy, 236
the ‘home control and ‘trip control’ conditions) (Mantel-Cox log-rank; χ 2 = 105.9, d.f.= 7, P = < 2e-237
16) (Fig 2). The pairwise comparison test showed that control individuals have a higher probability 238
of survival than irradiated individuals. In particular, the ‘trip control’ condition showed significant 239
differences with all the irradiation doses tested (80 Gy, p = 0.0 39; 100 Gy, p = 0.027; 120 Gy, p = 240
0.013; 140 Gy, p = 0.017; 160 Gy, p < 0.001; 180 Gy, p < 0.001; ‘home control’ condition, p = 241
0.014), with an average life of 71 days. Instead, the ‘home control’ condition showed significant 242
differences only with 160 Gy (p = 0.001), 180 Gy (p = 0.027), and the ‘trip control’ condition, with 243
an average life of 68 days. Significant differences were also observed in the longevity of males 244
irradiated at 80 Gy and those irradiated at 160 Gy (p < 0.001), 180 Gy (p < 0.001), and the ‘trip 245
lts
ey
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control’ condition. The longevity of individuals irradiated at 160 Gy is significantly different from 246
both control treatments and 80 Gy irradiation and also from 100 Gy (p < 0.001), 120 Gy ( p < 247
0.001), 140 Gy (p < 0.001) and 180 Gy (p = 0.013). Furthermore, we found that the longevity of 248
individuals irradiated at 180 Gy is significantly different from both control treatments, 80 Gy and 249
160 Gy, and also from 100 Gy (p < 0.001), 120 Gy (p < 0.001), and 140 Gy (p < 0.001 ). The 250
average life of individuals irradiated at 160 Gy was 46 days and irradiated at 180 Gy was 55 days. 251
We found no significant differences between the dose irradiations 80, 100, 120 and 140 Gy, with an 252
average life of 63 days (Fig 2). 253
254
Fig 2. Irradiation effect on D. melanogaster male longevity. Kaplan-Meier curves showing the effect of 255
different irradiation doses on the longevity of D. melanogaster males. 256
257
3.3. Irradiation effect on D. melanogaster male’ courtship behavior 258
In the “no-choice” conditions, the mean (± SE) courtship time widely ranged from 16.70% (± 3.98) 259
(D. melanogaster irradiated at 160 Gy) up to 67.66% (± 8.30) (D. suzukii males) (Fig 3). The GLM 260
model showed significant differences in the average courtship time among conditions (Table 3). 261
Tukey's multiple comparison tests showed a significant difference between D. suzukii homospecific 262
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13
condition and the conditions with D. melanogaster irradiated at 160 Gy (z = 4.346, p = <0.001) and 263
180 Gy (z = 3.552, p = 0.002) and also a significant difference between D. melanogaster irradiated 264
at 80 Gy and 160 Gy (z = 2.697, p = 0.035). No significant differences were observed in terms of 265
courtship time between D. suzukii males and D. melanogaster males irradiated at 80 Gy (p > 0.05) 266
and between the courtship time of D. melanogaster irradiated at 80 and 180 Gy (p > 0.05) (Fig 3). 267
In the “choice” trials, the mean courtship times varied across treatments. In the conspecific 268
condition with two D. suzukii males, the mean courtship time was 24.23% (± 6.17) for one male and 269
16% (± 3.50) for the other. In the heterospecific condition with irradiated D. melanogaster males at 270
80 Gy, the D. suzukii male exhibited a mean courtship time of 12.60% (± 3.06), while the D. 271
melanogaster male displayed 31.83% (± 7.37). In the heterospecific condition with irradiated D. 272
melanogaster males at 160 Gy, the D. suzukii male showed a mean courtship time of 24% (± 4.88), 273
whereas the D. melanogaster male had 9.66% (± 4.61). In the heterospecific condition with D. 274
melanogaster males irradiated at 180 Gy, the courtship time was 12.59% (± 1.94) for the D. suzukii 275
male and 13.58% (± 5.68) for the D. melanogaster male (Fig 4). 276
The GLM analysis revealed significant differences in the average courtship time among conditions 277
(Table 4), and Tukey’s multiple comparisons test indicated a significant difference only between the 278
courtship times of irradiated D. melanogaster males irradiated at 80 Gy and 160 Gy (p = 0.016; Fig 279
4). The Wilcoxon rank sum test highlighted significant differences only in the total courtship time 280
between D. melanogaster males irradiated at 160 Gy and D. suzukii males (W = 82.5, p = 0.002) 281
(Fig 4). 282
283
Table 3. Irradiation effect on D. melanogaster male’ courtship time in “no-choice” 284
condition. GLM model values are shown. Values in boldface indicate significant differences. D. 285
suz = Drosophila suzukii; D. mel = Drosophila melanogaster. 286
Fixed Effects Estimate ±SE z Value p-Value
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(Intercept) 2.8151 0.2273 12,384 < 2e-16
D. mel 180 Gy 0.2592 0.3204 0.809 0.41853
D. mel 80 Gy 0.8595 0.3188 2.697 0.00069
D. suz
(homospecific condition) 1.3994 0.3220 4.346 1.39e-05
287
288
Table 4. Irradiation effect on D. melanogaster male’ courtship time in “choice” condition. 289
GLM model values are shown. Values in boldface indicate significant differences. D. suz = 290
Drosophila suzukii; D. mel = Drosophila melanogaster. 291
Fixed Effects Estimate ±SE z Value p-Value
(Intercept) 3.4604 0.2447 14,139 < 2e-16
D. suz 80 Gy -0.9271 0.3496 -2.652 0.00799
D. mel 160 Gy -1.1924 0.3513 -3.394 0.00068
D. suz 160 Gy -0.2828 0.3469 -0.815 0.41493
D. mel 180 Gy -0.8515 0.3538 -2.407 0.01609
D. suz 180 Gy -0.9279 0.3496 -2.654 0.00794
D. suz 1
(homospecific condition) -0.6934 0.3530 -1.964 0.04948
D. suz 2
(homospecific condition) -0.2730 0.3514 -0.777 0.43724
292
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293
Fig 3. Courtship comparison in the “no-choice” trials. Courtship of D. suzukii males toward D. suzukii294
females (pink column); courtship of D. melanogaster males toward D. suzukii females at different irradiation 295
doses (blue, green and orange columns). *** Tukey's multiple com- parison tests p < 0.001; ** Tukey's 296
multiple comparison tests p < 0.01; * Tukey's multiple comparison tests p-value < 0.05. Black dots are box -297
plot outliers. 298
299
kii
on
y's
-
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300
Fig 4. Courtship comparisons in “choice” trials. Time spent courting D. suzukii females by D. suzu kii301
males and irradiated D. melanogaster males at 80, 160 and 180 Gy. D. suz = D. suzukii males (pink 302
columns); D. mel 80 Gy = D. melanogaster males irradiated at 80 grey (blue column); D. mel 160 Gy = D. 303
melanogaster males irradiated at 160 grey (green column); D. mel 180 Gy = D. melanogaster males 304
irradiated at 180 grey (orange column). Black dots are box-plot outliers. * Tukey's multiple comparison 305
tests p-value < 0.05; ** Wilcoxon rank sum test p < 0.01. 306
307
4. Discussion 308
Finding the best irradiation dose is a crucial issue that requires careful evaluation to develop a 309
heterospecific SIT approach. We found that irradiation was highly effective at reducing fertility. All 310
irradiation doses led to a significant reduction in adult emergence with respect to the control 311
condition (Table 1; Fig 1). We observed at the lower irradiation dose tested (80 Gy), only a 17% (± 312
5.38) average residual fertility that decreases as the irradiation doses increase until reaching 0.47 (± 313
0.34) average residual fertility at the highest dose tested (180 Gy) (Table 1). These results are 314
consistent with previous findings. Studies about the effect of gamma rays on the sterility of D. 315
kii
nk
D.
es
on
a
ll
ol
(±
(±
re
D.
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17
melanogaster have been carried out in the 1960s and ‘70s. Henneberry (1963) (42) found that D. 316
melanogaster irradiated males at 160 Gy dose produced nonviable eggs after mating with non-317
irradiated females. Accordingly, Nelson (1973) (43) observed that at 120 Gy 99.3% fewer progeny 318
emerged than non-irradiated individuals. 319
A trade-off between the sterility and longevity of the irradiated males is critical in 320
optimizing classic and heterospecific SIT applications (44). The survival analysis showed that 321
irradiation significantly reduces the lifespan of D. melanogaster males, with the highest reductions 322
in longevity at the highest doses. Control individuals lived on average for 70 days, whereas males 323
irradiated at the highest doses (160–180 Gy) experienced a 50-day lifespan (Fig 2). This 324
observation aligns with prior studies indicating that irradiation-induced oxidative stress and cellular 325
damage can impair physiological functions, shortening lifespan (45). Nelson et al. (1973) (43) also 326
reported decreased longevity in irradiated D. melanogaster, with a similar reduction in lifespan at 327
the highest dose tested of 150 Gy. The dose-dependent decrease in longevity must be carefully 328
considered when applying SIT since male competitiveness may be compromised if they do not 329
survive long enough to mate effectively in the wild. A reduction in the average lifespan of D. 330
melanogaster from 70 in the controls to 50 days at the highest radiation doses can be seen unlike to 331
compromise the effectiveness of SIT, as frequent releases of sterile individuals are typically part of 332
the strategy. For instance, regarding screwworm Cochliomyia hominivorax (Coquerel), the releases 333
have to occur weekly to maintain the critical ratio or even twice a week for the Mediterranean fruit 334
fly and tsetse Glossina austeni (Wiedemann) (46–48). We want to highlight that this study was not 335
addressed to assess the longevity of sterile individuals in field conditions, which can be lower than 336
in protected field-cage situations, where sterile males have easy access to food and are protected 337
from predation in the laboratory (49). This aspect certainly warrants further investigation. 338
The last part of this study was designed to assess the heterospecific courtship behavior of 339
irradiated D. melanogaster males. A balance between sterility and behavioral competence when 340
selecting an irradiation dose for pest control is critical. If males lose the ability to court females, 341
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18
their sterility will have limited impact on population suppression, as seen in studies of other insect 342
species, such as the Queensland fruit fly ( Bactrocera tryoni Froggatt), where high doses impaired 343
sexual competitiveness (50). Our findings showed that irradiated D. melanogaster males retained 344
their ability to court D. suzukii females even at the highest irradiation doses, suggesting that 345
courtship behavior remains largely unaffected by irradiation. In the “no-choice condition”, however, 346
D. melanogaster males irradiated at 160 and 180 Gy exhibited significantly lower courtship activity 347
compared to D. suzukii males toward conspecific females (Table 3; Fig 3). Conversely, under the 348
“choice condition”, D. melanogaster males courted D. suzukii females as much as D. suzukii males, 349
even at the highest irradiation doses tested. Notably, D. melanogaster males irradiated at 160 Gy 350
showed reduced courtship toward D. suzukii females compared to D. melanogaster males irradiated 351
at 80 Gy and D. suzukii males, corroborating the observations made in the “no-choice condition” 352
(Fig 4). These results suggest two key points. First, the presence of D. melanogaster males seems to 353
influence the courtship behavior of D. suzukii males, as they courted conspecific females more in 354
the “no-choice condition” compared to the “choice condition”. The reduced courtship behavior 355
observed at a radiation dose of 160 Gy suggests that higher doses may lead to behavioral 356
impairments in D. melanogaster males. These impairments are likely attributable to physiological 357
alterations or disruptions in neural circuits essential for mating displays. Ionizing radiation is known 358
to damage neural pathways involved in courtship behavior, as evidenced in moths, where higher 359
doses often result in physiological defects that reduce their competitiveness with wild populations 360
(51,52). Radiation may also interfere with producing or expressing key biochemical and behavioral 361
signals. During courtship, D. melanogaster males emit specific biochemical signals, such as cis-362
vaccenyl acetate, along with behavioral signals like wing vibrations and pheromone release, to 363
stimulate female responses (53–55). Ionizing radiation may disrupt these signals, compromising the 364
male's ability to communicate with females effectively. Similar disruptions have been observed in 365
other pest species, such as Callosobruchus chinensis L. females and Anthonomus grandis 366
(Boheman) males, where radiation-induced impairments in mating signals led to reduced courtship 367
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19
and mating success (56,57). Consequently, irradiated D. melanogaster males may fail to elicit 368
appropriate responses from females, disrupting courtship and mating dynamics. In our study, while 369
D. melanogaster males irradiated at 160 Gy showed reduced courtship, males exposed to 180 Gy 370
courted D. suzukii females comparably to untreated D. suzukii males under both "no-choice" and 371
"choice" conditions (Figs 3 and 4). Additionally, the highest courtship percentage was observed at 372
the lowest tested dose of 80 Gy (Figs 3 and 4), supporting the notion that lower radiation doses may 373
preserve male courtship behavior more effectively. 374
Overall, our study highlights the complex interactions between irradiation, longevity, 375
sterility, and mating behavior in D. melanogaster and contributes to growing evidence of using 376
heterospecific SIT in pest control. Based on our results, the 80 Gy and 180 Gy radiation doses 377
appear most suitable for further investigation. At 80 Gy, we observed the highest courtship rates 378
and longest lifespan among the radiation doses tested. In comparison, at 180 Gy, we achieved the 379
greatest reduction in fertility. 380
For an effective SIT program, it is essential that sterile males survive for a long time in their 381
environment. Only in this way they can mate with a sufficient number of wild females and induce 382
sterility in the population. If their quality is compromised and their longevity reduced, more 383
frequent and larger-scale releases will be required to sustain a high overflooding ratio, ultimately 384
increasing operational costs (58). Studies on An. arabiensis and Ae. aegypti have highlighted 385
different factors influencing longevity. An. arabiensis was found to have a significantly shorter 386
lifespan in field settings compared to laboratory conditions, whereas Ae. aegypti exhibited a 387
stronger sensitivity to seasonality (59). Specifically, in a field experiment carried out in Vietnam, 388
Ae. aegypti populations demonstrated significantly higher survival rates during the cool or hot dry 389
seasons compared to the cool and wet seasons (60). Moreover, a synergistic effect of irradiation, 390
packing, and chilling was observed to compromise the longevity of An. arabiensis —an effect that 391
was not detected in Ae. aegypti (59). These results suggest that the impact of irradiation on lifespan 392
is highly species-dependent. In our case, it is essential first to assess the differences in D. 393
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melanogaster males' longevity kept under laboratory conditions and those exposed to environmental 394
conditions. This would allow us to better evaluate the lifespan reduction at 180 Gy and determine 395
whether it constitutes a limitation for SIT applications. Conversely, a higher residual fertility at 80 396
Gy than 180 Gy might be less restrictive given that we are not dealing with a pest or invasive 397
species. Unlike in standard SIT applications for pest control, achieving the high sterility levels 398
required to release pest males (as discussed by Bakri et al. 2021 (61) and Parker et al. 2021 (62)) 399
may not be necessary in this context. Based on these considerations, the present study has 400
demonstrated that an irradiation dose of 80 Gy seems to be more effective. However, further studies 401
are needed better to evaluate both longevity and mating performance under field conditions. 402
Greenhouses and other enclosed environments appear ideal for implementing the 403
heterospecific Sterile Insect Technique (h-SIT) to manage D. suzukii populations. Studies on 404
plastic- and mesh-covered tunnels have shown that mechanical barriers alone can significantly 405
reduce D. suzukii populations in these confined areas. This reduction is due not only to the physical 406
exclusion provided by the barriers but also to creating an unfavorable microclimate for the pest's 407
survival (63). Although complete exclusion cannot be achieved through mechanical barriers alone, 408
integrating h-SIT with these measures could enhance the overall effectiveness of biocontrol 409
strategies. 410
411
Conclusions
412
Our findings highlight the critical balance between sterility, longevity, and mating behavior in D. 413
melanogaster for heterospecific SIT applications. Among the tested doses, 80 Gy emerged as the 414
most effective, preserving male longevity and mating performance while significantly reducing 415
fertility. While 180 Gy achieved the highest sterility, the potential lifespan and courtship behavior 416
trade-offs warrant further evaluation. Future studies should focus on-field performance to refine SIT 417
protocols. Integrating h-SIT with mechanical barriers in controlled environments like greenhouses 418
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could enhance D. suzukii management, making 80 Gy a promising dose for practical 419
implementation. 420
421
Acknowledgments 422
We thank Alessandra Spanò, Elisa Michelangeli and Giulia Pezzi for their technical help. 423
424
425
426
427
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