Transgenerational hormetic effects of sublethal dose of flupyradifurone on the green peach aphid, Myzus persicae (Sulzer) (Hemiptera: Aphididae)

Both inhibitory and stimulatory (known as hormesis) effects of the sublethal flupyradifurone, a butenolide insecticide, on Myzus persicae Sulzer (Hemiptera: Aphididae) were investigated for incorporating it into integrated pest management (IPM). A leaf-dip bioassay showed that flupyradifurone was very toxic against adult M. persicae with a 48 h LC50 of 8.491 mg/L. Using the age-stage two-sex life table approach, we assessed the effects of LC25 of flupyradifurone on adult M. persicae and its progeny (F1 and F2). On the one hand, aphids exposed to flupyradifurone had significantly negative effects on the life history traits acrossing the generations, such as reduced the adult longevity and fecundity of F0, shortened the duration of third instar and fourth instar nymphs, preadult period and the pre-reproductive period of F1, and decreased the reproductive days and adult longevity of F2. On the other hand, stimulatory effects on the duration of pre-adult, adult reproductive days, and reproduction of F1 were observed in the flupyradifurone-treated aphids. Consistently with the stimulation on individual traits, a higher net reproductive rate (R0) of F1 and a shorter mean generation time (T) of F2 were observed in the flupyradifurone-treated aphids, although the other population parameters including the intrinsic rate of increase (r), finite rate of increase (λ) and T of F1 and R0, r and λ of F2 were not significantly affected. These results revealed that adult M. persicae exposed to sublethal concentration of flupyradifurone can induce hormetic effects on F1, and also cause negative effects on F2. Our results would be useful for assessing the overall effects of flupyradifurone on M. persicae and the hormetic effects should take into consideration when use flupyradifurone for control M. persicae.


Introduction
The green peach aphid, Myzus persicae Sulzer (Hemiptera: Aphididae), is one of the most destructive and cosmopolitan insect pest of economical crops [1]. The green peach aphid feeding can cause direct damage and may cause indirect damage through the transmission over 100 plant pathogenic viruses [2]. Control of M. persicae has been dependent the use of chemical insecticides which frequently resulted in development of resistance to various classes of insecticides, including organophosphates, carbamates, pyrethroids, and neonicotinoids [3,4]. Therefore, the insecticides with environment safety and different modes of action remain critical for control of M. persicae.
The novel butenolide insecticide flupyradifurone was discovered and developed by Bayer CropScience in 2012 [5]. Flupyradifurone acts as a partial agonist on insect nicotinic acetylcholine receptors (nAChRs) and reversibly binds to acetylcholine (ACh) [6,7], but is structurally distinct from the class of neonicotinoid insecticides [7]. It was introduced as an effective insecticide to control a broad range of sucking pests and lacks significant cross resistance to both imidacloprid and pymetrozine in CYP6CM1-mediated resistance of whiteflies [7,8]. Especially, it shows an excellent safety profile for honey bees [5]. Insects are exposed to both lethal and low or sublethal concentrations of insecticide residues under field conditions due to misapplication, pesticide drift, shielding by vegetation, or residual levels after dissipation in the environment [9], thus they may experience directly mortality and certain related sublethal effects [10,11]. Sublethal effects are defined as physiological and/or behavioral effects on individuals that survived from exposure to a pesticide at sublethal concentration [10,12]. On the one hand, sublethal effects of insecticides could affect population dynamics through impaired behaviors and physiological traits, such as reduce insect longevity and fecundity [10,13]. On the other hand, sublethal effects could increase fecundity after exposure to an insecticide and have been documented in several insect pests, such as M. persicae [14][15][16][17], Rhopalosiphum padi L. (Hemiptera: Aphididae) [18], and Frankliniella occidentalis Pergande (Thysanoptera: Thripidae) [19]. This stimulatory effects induced by insecticides is called "insecticide-induced hormesis". Hormesis is a biphasic dose-response phenomenon characterized by a low-dose stimulation and a high-dose inhibition and this hormetic response is a modest overcompensation to a disruption in homeostasis or of a direct stimulatory nature [20][21][22][23][24]. It was an adaptive response of generally similar quantitative features with respect to amplitude and range of stimulatory response [21,[25][26][27]. For example, the sublethal doses of imidacloprid and precocene can induce stimulation of reproduction of M. persicae, however, inhibition at high doses [14,16]. Flonicamid and thiamethoxan can prolong the duration of phloem ingestion of M. persicae at sublethal doses, whereas induce starvation or contact toxicity at high doses [28]. Further, some survivors with hormesis may develop resistance to the insecticide subsequently [18,19,29,30] and induce pest resurgence and outbreak [24,31,32].
Therefore, it is important to understand the sublethal effects on non-targeted arthropods and overall effects on targeted pests caused by pesticides. The flupyradifurone was recently introduced in markets and has proved to be especially effective against a wide range of homopterous insect pests, including M. persicae [7]. However, to date, the potential sublethal or hormetic effects of flupyradifurone on M. persicae are still unknown. To obtain a comprehensive understanding of the overall effects of flupyradifurone on M. persicae, we assessed the effects of a sublethal concentration (LC 25 ) of flupyradifurone on biological traits and demographic parameters of M. persicae using the age-stage, two-sex life table. This information would be important to enable a more effective use of this insecticide in management programs for M. persicae through improved understanding of its activity profiles.

Insects
The colony of M. persicae was established from apterous adults collected from Chinese cabbage (Brassica oleracea var. capitata L.) field in Fujian Province, China (Site: 26.90˚N, 119.46˚E) in February 2017. The insects were reared on vermiculite-cultured radish (Raphanus sativus L.) seedlings and maintained at 23 ± 1˚C, 65-75% relative humidity (RH), with a photoperiod of 16: 8 (L: D) h in the laboratory.

Insecticide and solutions
Flupyradifurone (CAS number: 951659-40-8) at the 96% of active ingredient was obtained from Bayer CropScience Co. Ltd (Monheim, Germany). Triton X-100 was purchased from Sigma-Aldrich Co. Ltd (Saint Louis, USA). All other chemicals and solvents used were technique grade reagents. A stock solution of flupyradifurone was prepared in acetone and diluted to appropriate concentrations with 0.05% (v/v) aqueous Triton X-100. In our bioassays, the acetone was controlled less than 1% in all final used insecticide solutions. The control was performed with distilled water containing 0.05% (v/v) Triton X-100.

Toxicity of flupyradifurone against M. persicae
A leaf-dip bioassay procedure initially developed by Moores et al. [33] and slightly modified by Tang et al. [17] was used to evaluate the acute toxicity of flupyradifurone to M. persicae. Briefly, wells of 12-well tissue-culture plates purchased from Corning (NY, USA) were filled with 2 mL of 2% (w/v) agar to keep the leaves turgid. Leaf discs (20 mm in diameter) were excised from fresh Chinese cabbage using a stainless steel cork borer. Leaf discs were individually dipped to insecticide-free (control) or serial insecticide solutions for 15 s and allowed to air dry for 1 h on disposable plastic gloves (Haimen Yangzi Medical Equipment Co., Ltd, Jiangsu Province, China). After drying, discs were placed upside down on agar in a 12-well tissue-culture plate. Each concentration was conducted three replicates, and 20 apterous adult aphids (� 24 h old) were transferred to each well with a soft paintbrush; each bioassay consisted of six concentrations. Each well with aphids was covered with Chinese art paper, also called Xuan paper, purchased from China Xuan Paper Co., Ltd (Anhui Province, China) to prevent aphid escaping. Then the plates with aphids were maintained at the laboratory conditions as described above. Mortality was examined after 48 h. Aphids that unable to move when carefully touched with a soft brush were considered dead. The LC 25 for subsequent experiments and LC 50 were calculated using PoloPlus 2.0 software (LeOra Software Inc., Berkeley, CA). The concentrationmortality relationship was considered valid (i.e., they fitted the observed data) when there was absence of significant deviation between the observed and the expected mortality (P > 0.05) [34].

Sublethal and transgenerational effects of leaf-dip exposure to flupyradifurone
A concentration (LC 25 ) of 2 mg/L approximate to 25% mortality level determined in preliminary bioassays was used in leaf-dip exposure experiments to evaluate the sublethal and transgenerational effects of flupyradifurone in M. persicae.
Chinese cabbage leaf discs (30 mm in diameter) were dipped in LC 25 of flupyradifurone or control solution for 15 s, air-dried for 1 h, and then placed in a plastic Petri dish (35 mm diameter) contained 2 mL of 2% (w/v) agar. Single apterous adult (� 24 h old) was randomly introduced to each treated leaf disc and more than 150 adults were treated in each group. Then, the Petri dishes were held in the laboratory conditions as described above. Mortality of adults was calculated after 48 h. The survivors were transferred to untreated leaf-discs individually for further study of sublethal effects of flupyradifurone in M. persicae.
In the experiments, the longevity and fecundity of F 0 adult aphids were recorded daily and newly laid nymphs were removed until the adult aphid died. In the succeeding progeny generations (F 1 and F 2 ), neonate nymphs with less than one-day of age (105 and 107 of F 1 and 64 and 110 of F 2 for the control and the flupyradifurone treatment, respectively) were randomly selected from the former generation and placed individually on the untreated Chinese cabbage leaf discs of Petri dishes for evaluating the transgenerational effects of flupyradifurone. Nymphs were observed throughout their development and total duration until adult emergence and survival were record. After the final ecdysis, adult survival and the number of F 1 or F 2 progeny were recorded daily until death. Leaf discs were replaced in each dish every five days with freshly untreated leaf discs during the experiments. All experiments were conducted at 23 ± 1˚C, 65-75% RH, and a photoperiod of 16: 8 (L: D) h. Age-stage, two-sex life tables were constructed from the data obtained in these experiments.

Statistical analysis
The raw data for each M. persicae individual collected in the life table study were analyzed using the age-stage two-sex life table theory [35,36]. The population parameters, including the intrinsic rate of increase (r), finite rate of increase (λ), net reproductive rate (R 0 ), the mean generation time (T), age-stage specific survival rates (s xj , where x is age and j is stage), age-specific survival rate (l x ), age-specific fecundity (m x ), adult pre-reproductive period (APRP), total pre-reproductive period (TPRP), reproductive days (R d ) (i.e., the number of days that adult produced offspring), age-specific maternity (l x m x ), age-stage specific life expectancy (e xj ), reproductive value (v xj ), were calculated using the computer program TWOSEX-MSChart [35][36][37]. The variances and standard errors of the population parameters were estimated using the bootstrap procedure [38] with 100,000 random resampling and difference of population parameters between control and insecticide treatment groups and between generations within each treatment group were compared by using the paired bootstrap test based on the confidence intervals of differences implemented in TWOSEX-MSChart [37,39,40]. All graphics were created using SigmaPlot 12.0 (Systat Software Inc., San Jose, CA, USA).

Toxicity of flupyradifurone on M. persicae adults
The toxicity of flupyradifurone to adult M. persicae was investigated at 48 h after leaf-dip exposure ( Table 1). The LC 50 value of flupyradifurone was estimated as 8.49 mg L -1 with a confidence interval of 5.33-12.39 mg L -1 and the LC 25 value was estimated as 2.10 mg L -1 with a confidence interval of 0.99-3.55 mg L -1 , respectively. The LC 25 value of 2 mg L -1 flupyradifurone was used as the sublethal concentration for the subsequent experiments.

Sublethal effects of flupyradifurone on the longevity and fecundity of parental (F 0 ) M. persicae
Short-term exposure (48 h) of adult M. persicae to LC 25 of flupyradifurone on leaf discs had a significant effect on the longevity and fecundity of the exposed individuals (F 0 generation) ( Fig  1). As compared to the control group, the adult longevity of the F 0 was significantly reduced from 9.96 d to 8.01 d by flupyradifurone treatment (P < 0.001; Fig 1). The fecundity of F 0 adults were also significantly reduced from 22.96 to 11.75 offspring/female after exposure to LC 25 of flupyradifurone (P < 0.001; Fig 1).

Transgenerational effects of flupyradifurone on development, longevity and fecundity of M. persicae
The development time, longevity, fecundity and total preadult survival rate of the succeeding progeny generations (F 1 and F 2 ) were evaluated ( Table 2). The sublethal concentration of flupyradifurone had significant effects on the development time and fecundity of F 1 generation M. persicae ( Table 2). The duration of first instar nymph (P = 0.0075) and reproductive days (P = 0.0006) of F 1 individuals were significantly prolonged by flupyradifurone treatment, as well as the fecundity of F 1 individuals was significantly stimulated by the sublethal flupyradifurone from 26.60 ± 1.32 to 35.25 ± 2.19 offspring/female (P = 0.0006; Table 2). Whereas, when compared to those of the control, the 48-h exposure of F 0 adult M. persicae to flupyradifurone significantly decreased the duration of third instar and fourth instar nymph, preadult duration, adult pre-reproductive period (APRP) and total pre-reproductive period (TPRP) in F 1 individuals (P < 0.01; Table 2) and significantly decreased the adult longevity, reproductive days and fecundity in F 2 individuals (P < 0.01; Table 2). However, no significant differences of F 1 generations were observed for the duration time of the second instar nymph, adult longevity, total longevity or total preadult survival rate between the control and flupyradifurone treatments. The total longevity, total preadult survival rate and the duration time of each instar nymph stage, preadult, APRP and TPRP of F 2 individuals in flupyradifurone treatment were not significantly different from the control (P > 0.05; Table 2).
In addition, the duration of first instar nymph, pre-adult period, adult longevity, TPRP, reproductive days and fecundity of F 2 individuals were significantly lower than that of F 1 individuals in the flupyradifurone treatment (P < 0.05; Table 2); By contrast, the APRP and total preadult survival rate of F 2 individuals were significant higher than that of F 1 individuals and no significant difference in duration time of second instar and third instar nymph and total longevity were observed between F 1 and F 2 generations in the flupyradifurone treatment group (P < 0.05; Table 2). Similarly, the duration time of each juvenile developmental stage (including 1 st , 2 nd , 3 rd and 4 th instar nymph stage and preadult period) and pre-reproductive period (including APRP and TPRP) of F 2 individuals were significantly lower than that of F 1 individuals in the control group (P < 0.05; Table 2); Whereas, the adult longevity, reproductive days and fecundity of F 2 individuals were significantly higher than that of F 1 individuals in the control (P < 0.05; Table 2).

Transgenerational effects of flupyradifurone on population parameters of M. persicae
The transgenerational effects of flupyradifurone (LC 25 ) on the population parameters of F 1 and F 2 generations were evaluated with bootstrap technique based on life tables (Table 3). The lower-case letters show significant differences between control and flupyradifurone treatments in the same generation, while the capital letters indicate the significant differences between generations within the same treatment (P < 0.05).
When compared to the control group, the net reproductive (R 0 ) of F 1 generation M. persicae was significantly increased after the sublethal flupyradifurone treatment (P = 0.0245; Table 3), and the intrinsic rate of increase (r) and finite rate of increase (λ) of F 1 were not significantly affected by flupyradifurone, although a stimulation tendency was observed in these two parameters (P = 0.0628; Table 3).The mean generation time (T) was not significantly affected in F 1 generation (P = 0.893; Table 3). However, compared with the control, the T of F 2 individuals was significantly decreased in the flupyradifurone treatment (P = 0.0084; Table 3). The R 0 of F 2 individuals was also showed a decline tendency from 34.56 in the control to 29.50 offspring/female in the flupyradifurone treatment, while the difference was not significant (P = 0.1313; Table 3). In addition, the r and λ of F 2 generation were not significantly affected by flupyradifurone as compared to that of the control (P = 0.9420 for r, P = 0.9407 for λ; Table 3). In addition, except no significant difference was observed in R 0 of the flupyradifurone treatment group, the r, λ and T were significantly increased from F 1 to F 2 generation within the control or the flupyradifurone treatment, as well as R 0 of F 2 was higher than R 0 of F 1 in the control (P < 0.001; Table 3).

Transgenerational effects of flupyradifurone on age-stage specific survival rate and fecundity of M. persicae
Age-stage survival rate curves (s xj ) show the probability that a newborn nymph will survive to age x and stage j. Obvious overlaps between different stages occurred in both flupyradifuronetreated and the control groups as a result of the variable developmental rates among individuals (Fig 2). Declined survival rates of each developmental stage of F 1 individuals were observed in the flupyradifurone treatment group as compared to the control group (Fig 2), however, the survival rates of the 2nd-(0.83) and 4th-(0.80) instar nymph of F 2 individuals in the flupyradifurone treatment were higher than that of the control (0.75 and 0.44 for 2 nd and 4 th instar nymph, respectively; Fig 2). The fourth instar nymph peak and the female adult peak of F 1 generation appeared at five days of age and nine days of age in the flupyradifurone treatment, while in the control at six days of age and at thirteen days of age, respectively (Fig 2). These showed the faster development in the flupyradifurone treatment group. Therefore, total development time of F 1 generational nymph in the flupyradifurone treatment (10 days) was shorter The small letters show significant differences between control and flupyradifurone treatments in each generation, while the capital letters indicate the significant differences between F 1 and F 2 generations within each treatment groups (P < 0.05).
than that of the control (13 days; Fig 2). For F 2 generation, a similar trend of s xj curves was observed between the control and flupyradifurone treatment groups (Fig 2). In addition, between generations, the adult survival rate of F 1 individuals was lower than F 2 individuals in each treatment group (Fig 2). The age-specific survival rate (l x ) demonstrates a simplified overview of the survival rate without accounting for the stage differentiation (Fig 3). The l x curves significantly declined on day 15 or 14 in F 1 or F 2 generation in both control and flupyradifurone treatment groups ( Fig  3). Interesting, a higher l x of F 1 generation were observed in flupyradifurone treated group from age 18 to 33 day (Fig 3), whereas a lower l x of F 2 generation in the flupyradifurone treatment was observed from age 15 to 36 day (Fig 3). The age-specific fecundity of the total population (m x ) and age-specific maternity (l x m x ) of the flupyradifurone treated M. persicae were higher than that of the control group in F 1 generation (Fig 3), while a similar trend of m x and l x m x of F 2 generation M. persicae were observed both in the treatment and the control groups (Fig 3).
The age-stage-specific life expectancy (e xj ) is the length of time that an individual of age x and stage j is expected to survive after age x (Fig 4). The life expectancy (e xj ) curves indicated that offspring (F 1 and F 2 ) of adult M. persicae with one-time flupyradifurone exposure could to survive longer than the control (Fig 4). In addition, the age-stage-specific reproductive value (v xj ) represents the devotion to future offspring of individuals from age x to stage j. A higher maximum reproductive value of each stage and a shorter preadult period of F 1 generation M. persicae were observed in the treatment group than those of the control (Fig 5), while in F 2 generation, except the 1st instar nymph, a lower v xj of each stage in the treatment group was observed than that of the control (Fig 5).

Discussion
The high toxicity of flupyradifurone has been reported for several sucking pests, including M. persicae, Aphis gossypii Glover (Hemiptera: Aphididae) and Bemisia tabaci Gennadius (Hemiptera: Aleyrodidae) [7]. In this study, flupyradifurone also showed a highly acute toxicity against adult M. persicae after 48 h leaf-dip exposure and the LC 50 was 8.491 mg/L and this LC 50 value is similar to that previously reported for Diaphorina citri Kuwayama (Hemiptera: Psyllidae), after 48 h leaf-dip exposure to flupyradifurone with 10.43 mg/L [41]. In addition to the lethal effects of insecticides, insect populations are frequently exposed to low concentrations of insecticides in the field due to the variable distribution and continuous degradation of insecticides [42,43]. Thus, sublethal effects of insecticides may increase or decrease insect population [10], assessing the development, survival, reproduction and behavioral response are important for overall understanding of the effects of flupyradifurone for IPM. In this study, an attempt was made to assess sublethal effects on life table characteristics of M. persicae over subsequent generations after exposed M. persicae adult to sublethal flupyradifurone for 48 h.
Sublethal effects that reduced fecundity and longevity, and altered behavior were usually observed in most insect pests after exposure to sublethal concentration of insecticides [10,[44][45][46]. For example, endosulfan can significantly reduce fecundity of Apolygus lucorum Meyer-Dür (Hemiptera: Miridae) after treated with sublethal concentrations [47] and buprofezin reduce adult longevity of B. tabaci by sublethal doses [48]. Similarly, in the present study, when initial M. persicae adult was exposed to leaf discs treated with sublethal concentrations of flupyradifurone, significant reductions in the fecundity and adult longevity of F 0 generation M. persicae were observed and the reproductive days, adult longevity, and fecundity were significantly shortened or reduced in the subsequent F 2 generation, although no significant effects on the development time of each nymph stage and survival rates were found in F 2 . Moreover, these adverse effects on F 2 individual aphids were translated to their population parameters including a lower R 0 and mean generation time (T) and showed that sublethal concentrations of flupyradifurone suppressed the population growth of F 2 generation M. persicae. Similar sublethal effects of insecticides on population growth have been reported in several insect pests, such as A. gossypii [49], A. lucorum [50], B. tabaci [51], Brevicoryne brassicae L. (Hemiptera: Aphididae) [52], Bradysia odoriphaga Yang et Zhang (Diptera: Sciaridae) [53] and M. persicae [54,55]. The negative sublethal effects may be due to increased biological fitness cost and also provide evidence that sublethal concentrations of flupyradifurone did have significantly sublethal and transgenerational effects on M. persicae.
Insecticide-induced hormesis that increased fecundity or change insect behavior have been reported in A. gossypii with bifenthrin [56], citrus thrip, Scirtothrips citri Moulton (Thysanoptera: Thripidae), with dicofol or malathion [57], mite, Tetranychus urticae Koch (Acari: Tetranychidae), with imidacloprid [58], and the brown planthopper, Nilaparvata lugens Stäl (Hemiptera: Delphacidae) [59,60] after exposure to low or sublethal concentrations of insecticides. In the present study, significantly increased fecundity and more reproductive days were observed in F 1 adults, indicating that sublethal concentration of flupyradifuron has a stimulatory effect (i.e., hormesis) on reproduction of F 1 generation M. persicae following parental adults 48-h exposure. Similar stimulatory effects on reproduction of M. persicae in offspring generations have been documented in response to sublethal concentration of several insecticides, including azinphosmethyl [61], azadirachtin [55], imidacloprid [55,62], and sulfoxaflor [17]. Additionally, in the present study, the sublethal concentration of flupyradifuron significantly affected the F 1 generation population growth, notably through a significantly shortened duration of third instar and fourth instar nymph, preadult period and pre-reproductive periods (APRP and TPRP), a significantly prolonged reproductive days and an increased fecundity. The sum of these effects on F 1 individual aphids translated to higher population parameters, including net reproductive rate (R 0 ), intrinsic rate of increase (r) and finite rate of increase (λ). These increased population parameters and stimulated reproduction indicated that sublethal concentration of flupyradifuron could to stimulate population growth of M. persicae in F 1 generation via maternal effects. Similarly, the reproduction of Daphnia carinata King (Diplostraca: Daphnidae) was negatively affected in the parental generation following exposure to low concentrations of chlorpyrifos, while a hormesis effect was observed for all reproductive parameters in the second generation [63] and the females of Chironomus riparius Kieffer (Diptera: Chironomidae) exposed to low tributylin concentrations for multiple generations significantly laid more eggs in the subsequent generations and acquired a higher tolerance towards the stressor [64]. These results suggested that sublethal effects on biological fitness may increase by exposure to low concentrations of insecticides.
Interestingly, in the present study, 48-h exposures of adult M. persicae (F 0 ) to sublethal concentration of flupyradifuron can significantly stimulate fecundity in the following F 1 generation, whereas reduced fecundity and adult longevity were observed in F 0 and F 2 generations, and no significant effects on development time of each instar nymph and population growth (R 0 ) were found between the treatment and control in F 2 generations. These results suggested that biological tradeoffs in resource allocation occurred across generations. Similarly, when M. persicae adults exposed to low/sublethal concentrations of azinphos-methyl [65], imidacloprid [15,62] and sulfoxaflor [17], this delayed stimulation of reproduction phenomenon was also observed in the subsequent generation of M. persicae, while not observed in initial adults. We hypothesized that the exposure of adult M. persicae to sublethal concentration of insecticides may: remove individuals of low fitness, cost biological fitness to cope with the stress of flupyradifurone in F 0 ; and result in stimulating reproduction (i.e. hormesis) and higher reproduction of F 1 progeny to overcompensate physiologically for their disrupted homeostasis via maternal effects, to optimize resource allocation between self-maintenance and reproductive output; and possibly restore homeostasis in F 2 generation. This no long-term fitness cost for the stimulatory response in early generations was also been demonstrated for imidacloprid in M. persicae [23,66]. Therefore, hormesis induced by sublethal concentrations of flupyradifuron may lead to secondary population outbreaks of M. persicae.
In conclusion, our results indicated that LC 25 concentration of flupyradifurone has transgenerational hormesis on M. persicae across three generations. The sublethal exposure of parental aphids resulted in significantly increase of duration of 1st instar nymph, reproductive days, fecundity and population parameters R 0 in F 1 generation and recovery R 0 to control level and reduced T in F 2 generation. These suggested that short-term exposure of the sublethal concentration of flupyradifurone might induce hormesis of M. persicae and this hormesis may lead to pest resurgence [57,67]. Because hormetic effects can be taken in form of shortened development, higher survival rate, or higher fecundity, these factors are not independent from each other and should not be analyzed separately [68,69]. Since life table analysis integrated all these factors in population parameters, it is the most important tool for an overall evaluation of population fitness and hormesis [17,70]. Nevertheless, given that the genetic variation in field populations is naturally greater than that of laboratory strains, the situation in the field may be more complex and further investigations on sublethal effects of this insecticide on M. persicae in the field are advisable. Consequently, flupyradifurone was very toxic against M. persicae M. persicae at the present study, but insecticide-induced hormesis should be taken into consideration, which may potentially occur after application of flupyradifurone for control M. persicae in the field.