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Sublethal effects of indoxacarb and beta-cypermethrin on Rhopalosiphum padi (Hemiptera: Aphididae) under laboratory conditions.

Rhopalosiphum padi (L.) (Hemiptera: Aphididae) is one of the most important pests of wheat because it causes direct crop damage through phloem feeding and indirect damage by honeydew contamination and associated fungal growth, or by vectoring plant viruses that cause yellow dwarf in winter cereals (Barley yellow dwarf virus, BYDV) (Savaris et al. 2013; Schliephake et al. 2013). Due to global warming, it is expected that insect-transmitted viruses will gain more importance (Schliephake et al. 2013). For instance, longer and warmer periods in autumn can lead to longer flight activities of the vectors resulting in an increased risk of winter cereals to become infected by these viruses (HabekuR et al. 2009). In fact, the current population profile of wheat aphids differs from that recorded in past decades (1970-1990). In recent years, R. padi has become one of the most frequent species on cereal crops and is abundant throughout all development stages of wheat plants (Parizoto et al. 2013; Savaris et al. 2013). Increased levels of damage by R. padi have been recorded in wheat-growing regions in China, especially in southern China (Zhang et al. 2007; Lu et al. 2009).

Although chemical control is still the main means of R. padi management, the escalating use of chemical pesticides had caused resistance of this pest to various insecticides (Zhang et al. 2007; Lu et al. 2009; Zuo et al. 2016). Hence, R. padi may probably be exposed to sublethal concentrations of insecticides under field conditions, and this may lead to sublethal effects. It is known that sublethal concentrations of insecticides can impair fundamental behavioral and physiological traits of the target insects such as activity, appetite, foraging behavior, and fecundity (Wang et al. 2008a; Qu et al. 2014). Sublethal concentrations of insecticides leading to pest outbreaks in the field have been reported in many pests (Reissig et al. 1982; Tripathi & Sachan 1990; Zhang et al. 2010). For example, Bartlett (1968) reported that a sublethal level of organochlorine and organophosphorus insecticides could cause aphid resurgence. Sublethal concentrations of imidacloprid and azadirachtin have been reported to increase survival and reproductive ability of Myzus persicae (Sulzer) (Hemiptera: Aphididae) (Cutler et al. 2006; Wang et al. 2008b). However, sublethal effects can also be manifested as reductions in lifespan, development rate, fertility, fecundity and other demographic parameters (Stark & Banks 2003; Lashkari et al. 2007), thereby potentially influencing the efficacy of pest control tactics. Sublethal concentrations of azadirachtin significantly reduced the longevity and fecundity of the pea aphid, Acyrthosiphon pisum Harris (Hemiptera: Aphididae) (Stark & Rangus 1994). Imidacloprid was shown to disrupt Bemisia tabaci (Gennadius) (Hemiptera: Aleyrodidae) population dynamics, slow population increase, and reduce infestation levels at low concentrations (He et al. 2011).

Beta-cypermethrin is classified as a toxicity class II (pyrethroid) insecticide, and it represents one of the main options for controlling aphids on cereals in China (Zhang et al. 2008; Shuai & Wang 2005). Rotational use of various insecticides or use of new insecticides that have different mechanisms of action can potentially reduce onset of resistance of R. padi to pyrethroids and maintain toxicity of pyrethroids to R. padi. Indoxacarb is an oxadiazine insecticide effective against a broad spectrum of insect pests and has low toxicity to non-target organisms (Dinter & Wiles 2000). These 2 kinds of pesticides are nerve agents, but their mechanisms of action are different. Beta-cypermethrin targets the voltage-gated sodium channels of insect neurons where they alter the activation/inactivation kinetics of the channel and cause disruption to normal nerve signaling, leading to paralysis and death (Soderlund & Bloomquist 1989). The metabolite of indoxacarb, so-called DCJW, is known to block the sodium channel of the target's nerve cells and to inhibit sodium currents in cultured insect neurons (Tsurubuchi et al. 2001).

Choosing pesticides for controlling pests based on integrated pest management requires information on the efficacy and potential risks of insecticides in populations of insect pests and non-target organisms (Qu et al. 2014). Life table parameters are recommended as a means to assess the sublethal effects and toxicological studies at the population level (Stark & Rangus 1994; Stark & Banks 2003). However, potential sublethal effects of indoxacarb and beta-cypermethrin on R. padi are still unknown. The objective of this study was to evaluate the sublethal effects of indoxacarb and beta-cypermethrin on 2 successive generations of R. padi.

Materials and Methods


The relatively susceptible clone of R. padi was collected from Yangling, Shaanxi, in China. Insects were reared on wheat seedlings in the laboratory using the caging method at 25 [+ or -] 1 [degrees]C with a 16:8 h L:D photoperiod and relative humidity >80%. The colony had been reared in the laboratory for more than 3 yr.


Two insecticides were used in the present study: 96% beta-cypermethrin (Yancheng Nongbo Bio-technology Co. Ltd., Jiangsu, China) and 95% indoxacarb (Huzhou Nanxun Nonghuida Chemical Co. Ltd., Jiangsu, China).


Toxicity bioassays were conducted with apterous adult aphids by using the leaf dip method (Han et al. 2007). Serial dilutions (mg/L) of the active ingredient of the test compounds were prepared using 0.1% Triton X-100 surfactant in water. Wheat leaves with apterous adult aphids were dipped in the dilutions of those compounds for 10 s. After 10 s, the leaves were removed from the solution and residual solution droplets on the leaves were adsorbed off with clean, dry filter paper pieces. The treated leaves were then transferred to plastic Petri dishes lined with moistened filter paper. Three replicates of 30 to 50 aphids were used for each insecticide concentration and for each of 5 serial concentrations. Leaves dipped in 0.1% Triton X-100 were used as controls. During and after the treatment, aphids were kept at a constant temperature of 25 [+ or -] 1 [degrees]C with a photoperiod of 16:8 h L:D. At 24 h post-treatment, mortality was scored. Aphids failing to exhibit movement after a gentle probe were considered dead. Data were analyzed by probit analysis using SPSS software (SPSS Inc. 2008).


According to the results of the toxicity bioassays, sublethal LC10 and LC30 concentrations of beta-cypermethrin were used at 0.39 and 0.92 mg/L, respectively, and those of indoxacarb were used at 0.14 and 0.42 mg/L, respectively. Wheat leaves with 100 to 120 aphids of mixed stages were dipped in LC10 and LC30 concentrations of indoxacarb and beta-cypermethrin for 10 s and the control, as described above. Twenty-four h after treatment, 30 survivors of wingless 4th instar nymphs or newly molted adults that had not undergone reproduction were selected and transferred to fresh, untreated leaves placed in plastic Petri dishes lined with moistened filter paper. Each Petri dish received only 1 aphid. A high relative humidity was maintained in the plastic Petri dish by periodically adding water to the filter paper. Leaves were replaced on a daily basis until the death of the last individual. The development, survival, and fecundity of individual aphids were recorded every 12 h until death. Fifty F1 nymphs were randomly selected from each leaf of each treatment and moved to separate plastic Petri dishes containing leaves. The development, survival, and fecundity of F1 individual aphids were recorded as described above.


Data were corrected for control mortality using Abbott's formula (Abbott 1925) before analysis, and analyzed by probit analysis (Finney 1971) using the software SPSS (SPSS Inc. 2008). The raw life history data of all individuals of this study were pooled and analyzed according to the age-stage, two-sex life table and the method described by Chi & Su 2006. The development time, longevity, and fecundity, and their mean values and standard errors were estimated using the bootstrap method included in the computer program TWOSEX-MSChart (Chi 2005). Treatment means were compared statistically using analysis of variance (ANOVA) and separated, whenever appropriate, by the Tukey test at the P = 0.05 level in SPSS (SPSS Inc. 2008). Population parameters were also calculated, and their means, standard errors, and significance differences were estimated with the bootstrap technique using TWOSEX-MSChart (Chi 2005). Means were compared using ANOVA and separated, whenever appropriate, using the Tukey test (P < 0.05) in SPSS (SPSS Inc. 2008).



The results of the leaf dip method with 95% confidence limits were obtained for apterous adults of R. padi at 24 h after treatment (Table 1). The LC10 and LC30 values of indoxacarb were 0.14 and 0.42 mg/L, respectively, after 24 h. The LC10 and LC30 values of beta-cypermethrin were 0.39 and 0.92 mg/L, respectively, after 24 h. For both insecticides, the LC10 and LC30 values were used to evaluate the sublethal effects on R. padi (Table 1).


The fecundity and longevity of adults of R. padi were significantly affected by the various beta-cypermethrin and indoxacarb concentrations that were evaluated (Table 2). The fecundity and longevity of R. padi exposed to B-LC30 were lowest. There were significant differences between the 4 treatments and the control group in mean longevity and reproduction of aphids (F = 13.15; df = 4,145; P < 0.001 and F = 23.55; df = 4,145; P < 0.001, respectively). Mean adult longevity of the R. padi F0 generation decreased by 50.75, 68.96, 30.68, and 40.61%, whereas mean fecundity of the R. padi F0 generation decreased by 65.93, 76.67, 47.70, and 54.30% after treatment with B-LC10, B-LC30, I-LC10 and I-LC30 respectively.


Development times of 1st to 4th instar nymphs were compared between all treatments (Fig. 1). The total development time of nymphs treated with sublethal concentrations of both insecticides was significantly longer compared with the control treatment (F = 12.14; df = 4,240; P < 0.001) (Fig. 1). Compared with the control, the B-LC10, BLC30, I-LC10 and I-LC30 treatments significantly increased the average development period of the nymphal stage of the R. padi F1 generation by 0.86, 0.67, 0.45, and 0.46 d, respectively (Fig. 1). Development time of 1st instar nymphs was significantly affected by beta-cypermethrin treatments and I-LC30 treatment, but no differences were noted between the I-LC10 treatment and the control group (F = 36.05; df = 4,245; P < 0.001) (Fig. 1). Development time of 2nd instar nymphs was not significantly affected by beta-cypermethrin and indoxacarb, except for the I-LC30 treatment, in which development time was shorter than in other treatments (F = 5.85; df = 4,238; P < 0.001) (Fig. 1). Development time of 3rd instar nymphs was significantly different between the I-LC10 treatment and the other treatments (F = 3.66; df = 4,238; P = 0.006). The total development time of 4th instar nymphs was significantly prolonged in indoxacarb treatments (F = 21.73; df = 4,235; P < 0.001). The B-LC30 treatment exerted significant effects on the longevity and reproduction of the R. padi F1 generation compared with the control treatment (Table 3) (F = 2.65; df = 4,238; P = 0.034 and F = 9.02; df = 4,233; P < 0.001, respectively).

Age-specific survival rate (lx) and age-specific fecundity of the total population (mx) were also measured (Fig. 2). The curves of lx in the BLC30 treatment group declined significantly from day 6. However, the curves of lx in other treatment groups declined significantly from day 23. The mx curve of the treatment groups is consistent with that of the control group, wherein all curves display a tendency of ascending first around the day 4 and going up and down in succession.


The effects of beta-cypermethrin and indoxacarb on the life table of the F1 population of R. padi are shown in Table 4. Compared with the control treatment, the intrinsic rate of increase (r) decreased for all treatments, except for the LC10 concentration of the indoxacarb treatment (F = 16.72; df = 4,245; P < 0.001) (Table 4). The finite rate of increase ([lambda]) was 1.527, 1.432, 1.422, 1.491, and 1.474 [d.sup.-1] for control, B-LC10, B-LC30, I-LC10, and I-LC30 treatments, respectively, and signifi-cantly decreased after beta-cypermethrin and indoxacarb treatment (F = 23.09; df = 4,245; P < 0.001). In terms of gross reproductive rate (GRR), the beta-cypermethrin treatments had negative effects (53.76 and 51.03 offspring per individual for B-LC10 and B-LC30, respectively), as compared with the other treatment (61.37, 59.45, and 59.57 offspring per individual for control, I-LC10 and I-LC30, respectively) (F = 16.06; df = 4,245; P < 0.001).The net reproductive rate ([R.sub.0]) of R. padi was significantly depressed in the LC30 concentration of the indoxa-carb treatment (Table 4). The mean generation time (T) in the control was significantly shorter than in the insecticide treatments (F = 4.45; df = 4,245; P = 0.0017).


In this study, indoxacarb and beta-cypermethrin were similarly effective on apterous aphids, but sublethal effects of both insecticides on R. padi varied, possibly due to the different mechanisms of action of beta-cypermethrin and indoxacarb. Beta-cypermethrin behaves as a fast-acting neurotoxin in insects (Song et al. 2013), where as indoxacarb blocks the insect voltage-gated sodium channel by the N-decarbomethoxyllated metabolite (Wing et al. 2000). Indoxacarb is a new insecticide not only with strong field activity against Lepidoptera but also with high efficiency in controlling certain important sucking insects such as leafhopper species and aphids (Wing et al. 2000). Results of this study support the claim that indoxacarb can be used as a substitute for older insecticide classes to manage populations of R. padi.

In addition to direct mortality induced by pesticides, sublethal concentrations of insecticides may cause behavioral and physiological effects on the target pest (Desneux et al. 2007). Increased fecundity and reproduction after exposure to sublethal concentrations of insecticides have been reported (Morse 1998; Zanuncio et al. 2003; Cutler et al. 2009; Cho et al. 2011). This may be one of the mechanisms of pest resurgence (Cutler et al. 2009; James & Price 2002). Insect pest resurgence induced by sublethal effects of insecticides could lead to the application of additional pesticide treatments, thereby potentially exacerbating insecticide resistance development (Qin et al. 2013). However, our study found no clear evidence for stimulation of growth or reproduction in R. padi following the application of the sublethal concentrations of the evaluated insecticides. The R. padi population did not increase, at least in the F1 generation, after application of sublethal concentrations of beta-cypermethrin and indoxacarb. On the contrary, longevity and fecundity of parent adults of R. padi significantly decreased after treatment. The decreased longevity and fecundity of female parent adults was similar to the result obtained in the cabbage aphid, Brevicoryne brassicae (L.) (Hemiptera: Aphididae), treated with imidacloprid and pymetrozine (Lashkari et al. 2007) and the pea aphid, A. pisum, treated with imidacloprid (Hui et al. 2009). The reduced fecundity of R. padi observed in our study might be due either to a shorter life span or to detrimental effects on the female's sexual organs or ovipositing mechanism; however, mechanisms involved were not studied here. Longevity and F1 generation were also affected by sublethal concentrations of beta-cypermethrin and indoxacarb, particularly by the B-LC10 treatment, which significantly reduced the longevity and fecundity of the aphid. These results may play an important role in the control of aphid pests by prolonging the efficacy of beta-cypermethrin and indoxacarb throughout the growing season.

The various insecticide treatments had different sublethal effects on the aphids. The differences were possibly caused by the different mechanisms of action of beta-cypermethrin and indoxacarb. Additionally, differences in residue levels in the bodies of mother aphids could also influence the results. Beta-cypermethrin treatments had greater influence on the development time of 1st instar nymphs than indoxacarb treatments. It is possible that beta-cypermethrin may suppress embryogenesis indirectly through adults and more effectively than indoxacarb (Tan et al. 2012). It is therefore conceivable that the sublethal effects observed on nymphs of the F1 generation may be due to penetration of the insecticides into the embryo.

Life table assays provided more detailed information on the side effects of the insecticides evaluated. Application of beta-cypermethrin and indoxacarb to parent aphids reduced r, [R.sub.0], and GRR of the F1 generation and prolonged T of the F1 generation in this study (Table 4). This finding is in agreement with results by Song et al. (2013) with Plutella xylostella (L.) (Lepidoptera: Plutellidae) after treatment with beta-cypermethrin and indoxacarb.

This study also showed that aside from lethal effects, beta-cypermethrin and indoxacarb cause multiple sublethal effects. Betacypermethrin and indoxacarb not only had marked effects on parent adults of R. padi but also had adverse effects on development and reproduction of individuals in the F1 generation. These findings indicate that indoxacarb could be used as an alternative or rotational pesticide option targeting pyrethroid-resistant R. padi populations in the field. It not only has a unique mechanism of action but also does not seem to stimulate aphid reproductive potential, potentially resulting in good control of R. padi. However, further studies are necessary to investigate the possible effect on digestion and ovaries and the potential mechanisms of physiological and behavioral effects by pesticides.


This work was funded by the National Natural Science Foundation of China (Grant No. 31272036, 31471766), the Doctoral Program Foundation of Institutions of Higher Education of China (20110204110001), and the National Key Technology R&D Program (No. 2012BAK11B03).

References Cited

Abbott W. 1925. A method of computing the effectiveness of an insecticide. Journal of Economic Entomology 18: 265-267.

Bartlett BR. 1968. Outbreaks of two-spotted spider-mites and cotton aphids following pesticide treatment. I. Pest stimulation vs. natural enemy destruction as the cause of outbreaks. Journal of Economic Entomology 61: 297-303.

Chi H. 2005. TWOSEX-MSChart: a computer program for the age-stage, twosex life table analysis. National Chung Hsing University, Taichung, Taiwan. http://140.120 197.

Chi H, Su HY. 2006. Age-stage, two-sex life tables of Aphidius gifuensis (Ashmead) (Hymenoptera: Braconidae) and its host Myzuspersicae (Sulzer) (Homoptera: Aphididae) with mathematical proof of the relationship between female fecundity and the net reproductive rate. Environmental Entomology 35: 10-21.

Cho SR, Koo HN, Yoon C, Kim GH. 2011. Sublethal effects of flonicamid and thiamethoxam on green peach aphid, Myzus persicae and feeding behavior analysis. Journal of the Korean Society for Applied Biological Chemistry 54: 889-898.

Cutler GC, Scott-Dupree C, Tolman J, Harris C. 2006. Toxicity of the insect growth regulator novaluron to the non-target predatory bug Podisus maculiventris (Heteroptera: Pentatomidae). Biological Control 38: 196-204.

Cutler CG, Ramanaidu K, Astatkie T, Isman MB. 2009. Green peach aphid, Myzus persicae (Hemiptera: Aphididae), reproduction during exposure to sublethal concentrations of imidacloprid and azadirachtin. Pest Management Science 65: 205-209.

Desneux N, Decourtye A, Delpuech JM. 2007. The sublethal effects of pesticides on beneficial arthropods. Annual Review of Entomology 52: 81-106.

Dinter A, Wiles JA. 2000. Safety of the new DuPont insecticide, indoxacarb to beneficial arthropods: an overview. Bulletin Organisation Internationale de Lutte Biologique et Integree/Section Regioale Ouest Palearctique 23: 149-156.

Finney DJ. 1971. Computer and other techniques, pp. 80-90 In Finney DJ [ed.], Probit Analysis. Cambridge University Press, New York, New York.

HabekuR A, Riedel C, Schliephake E, Ordon F. 2009. Breeding for resistance to insect-transmitted viruses in barley--an emerging challenge due to global warming. Journal fur Kulturpflanzen 61: 53-61.

Han XL, Gao ZL, Dang ZH, Li YF, Chi GT, Pan WL. 2007. Studies on sensitivity of chloronicotinyl insecticides in the grain aphid, Sitobion avenae (Fab.) from different areas. Acta Agriculturae Boreali-Sinica 22: 157-160.

He Y, Zhao J, Wu D, Wyckhuys KA, Wu K. 2011. Sublethal effects of imidacloprid on Bemisia tabaci (Hemiptera: Aleyrodidae) under laboratory conditions. Journal of Economic Entomology 104: 833-838.

Hui JJ, Liu CZ, Meng YF, Chen J. 2009. Sublethal effects of imidacloprid to Acyrthosiphon pisum. Plant Protection 35: 86-88.

James DG, Price TS. 2002. Fecundity in twospotted spider mite (Acari: Tetranychidae) is increased by direct and systemic exposure to imidacloprid. Journal of Economic Entomology 95: 729-732.

Lashkari MR, Sahragard A, Ghadamyari M. 2007. Sublethal effects of imidacloprid and pymetrozine on population growth parameters of cabbage aphid, Brevicoryne brassicae on rapeseed, Brassica napus L. Insect Science 14: 207-212.

Lu YH, Yang T, Gao XW. 2009. Establishment of baseline susceptibility data to various insecticides for aphids Rhopalosiphum padi (Linnaeus) and Sitobion avenae (Fabricius) (Homoptera: Aphididae) by the method of residual film in glass tube. Acta Entomologica Sinica 52: 52-58.

Morse JG. 1998. Agricultural implications of pesticide-induced hormesis of insects and mites. Human and Experimental Toxicology 17: 266-269.

Parizoto G, Rebonatto A, Schons J, Lau D. 2013. Barley yellow dwarf virus-PAV in Brazil: seasonal fluctuation and biological characteristics. Tropical Plant Pathology 38: 11-19.

Qin X, Zhang J, Liu Q, Chen Y, Zhang R. 2013. Sublethal effects of paichongding on Nilaparvata lugens (Homoptera: Delphacidae). Journal of Economic Entomology 106: 10-15.

Qu YY, Xiao D, Li JY, Chen Z, Biondi A, Desneux N, Gao XW, Song DL. 2014. Sublethal and hormesis effects of imidacloprid on the soybean aphid Aphis glycines. Ecotoxicology 24: 479-487.

Reissig WH, Heinrichs EA, Valencia SL. 1982. Effects of insecticides on Nilaparvata lugens and its predators: spiders, Microvelia atrolineata and Gyrtorhinus lividipennis. Environmental Entomology 11: 193-199.

Savaris M, Lampert S, Salvadori JR, Lau D, Pereira PRVS, Smaniotto MA. 2013. Population growth and damage caused by Rhopalosiphum padi (L.) (Hemiptera, Aphididae) on different cultivars and phenological stages of wheat. Neotropical Entomology 42: 539-543.

Schliephake E, Habekuss A, Scholz M, Ordon F. 2013. Barley yellow dwarf virus transmission and feeding behaviour of Rhopalosiphum padi on Hordeum bulbosum clones. Entomologia Experimentalis et Applicata 146: 347-356.

Shuai X, Wang JJ. 2005. Change in esterase activity and content during the selection of resistance to alphamethrin in Myzus persicae. Zoological Research 26: 101-105.

Soderlund DM, Bloomquist JR. 1989. Neurotoxic actions of pyrethroid insecticides. Annual Review of Entomology 34: 77-96.

Song L, Zhang JM, Lv YB. 2013. Sublethal effects of indoxacarb and beta-cypermethrin on Plutella xylostella (Lepidoptera: Plutellidae). Acta Entomologica Sinica 56: 521-529.

SPSS Inc. 2008. SPSS Statistics for Windows, Version 17.0. Chicago, Illinois.

Stark JD, Banks JE. 2003. Population-level effects of pesticides and other toxicants on arthropods. Annual Review of Entomology 48: 505-519.

Stark JD, Rangus TM. 1994. Lethal and sublethal effects of the neem insecticide formulation, "Margosan-O", on the pea aphid. Pesticide Science 41: 155-160.

Tan Y, Biondi A, Desneux N, Gao XW. 2012. Assessment of physiological sublethal effects of imidacloprid on the mirid bug Apolygus lucorum (Meyer-Dur). Ecotoxicology 21: 1989-1997.

Tripathi N, Sachan G. 1990. Effect of concentrations of insecticides on the growth and development of mustard aphid, Lipaphis erysimi Kalt. Indian Journal of Entomology 52: 63-68.

Tsurubuchi Y, Zhao X, Nagata K, Kono Y, Nishimura K, Yeh JZ, Narahashi T. 2001. Modulation of tetrodotoxin-resistant sodium channels by dihydropyrazole insecticide RH-3421 in rat dorsal root ganglion neurons. Neurotoxicology 22: 743-753.

Wang XY, Yang ZQ, Shen ZR, Lu J, Xu WB. 2008a. Sublethal effects of selected insecticides on fecundity and wing dimorphism of green peach aphid (Homoptera: Aphididae). Journal of Applied Entomology 132: 135-142.

Wang Y, Chen J, Zhu YC, Ma C, Huang Y, Shen J. 2008b. Susceptibility to neonicotinoids and risk of resistance development in the brown planthopper, Nilaparvata lugens (Stal) (Homoptera: Delphacidae). Pest Management Science 64: 1278-1284.

Wing KD, Sacher M, Kagaya Y, Tsurubuchi Y, Mulderig L, Connair M, Schnee M. 2000. Bioactivation and mode of action of the oxadiazine indoxacarb in insects. Crop Protection 19: 537-545.

Zanuncio TV, Serrao JE, Zanuncio JC, Guedes RNC. 2003. Permethrin-induced hormesis on the predator Supputius cincticeps (Stal, 1860) (Heteroptera: Pentatomidae). Crop Protection 22: 941-947.

Zhang J, Yuan FH, Liu J, Chen HD, Zhang RJ. 2010. Sublethal effects of nitenpyram on life table parameters and wing formation of Nilaparvata lugens (Stal) (Homoptera: Delphacidae). Applied Entomology and Zoology 45: 569-574.

Zhang L, Shi J, Gao X. 2008. Inheritance of beta-cypermethrin resistance in the housefly Musca domestica (Diptera: Muscidae). Pest Management Science 64: 185-190.

Zhang NQ, Yu LC, Wang MY, Liu YH. 2007. Resistance situation of wheat aphid and its synthetic control. Acta Agriculturae Jiangxi 19: 50-52.

Zuo Y, Wang K, Zhang M, Peng X, Pinero JC, Chen M. 2016. Regional susceptibilities of Rhopalosiphum padi (Hemiptera: Aphididae) to ten insecticides. Florida Entomologist (in press).

Yayun Zuo (1) ([section]), Kang Wang (1) ([section]), Fangfei Lin (1) ([section]), Yuting Li (1), Xiong Peng (1), Jaime C. Pinero (2), and Maohua Chen (1) *

(1) Key Laboratory of Crop Pest Integrated Pest Management on the Loess Plateau of Ministry of Agriculture, College of Plant Protection, Northwest A&F University, 3 Taicheng Road, Yangling District, Shaanxi Province 712100, China; E-mail: (Y. Z.), (K. W.), (F. L.), (Y. L.), (M. C.)

(2) Lincoln University, Cooperative Research & Extension, 900 Chestnut St, Jefferson City, Missouri 65101, USA; Email: (J. C. P)

* Corresponding author; E-mail: (M. C.)

([section]) These 3 authors contributed equally to this work

Caption: Fig. 1. Comparisons of development times of nymphs (mean [+ or -] SE) across all treatments (different letters indicate significant differences between populations at the P < 0.05 level). CK: control treatment; B-LC10: LC10 of beta-cypermethrin; B-LC30: LC30 of beta-cypermethrin; I-LC10: LC10 of indoxacarb; I-LC30: LC30 of indoxacarb.

Caption: Fig. 2. Effects of beta-cypermethrin and indoxacarb sub-lethal concentrations on age-specific survival rate and age-specific fecundity of Rhopalosiphum padi F1 generation. CK: control treatment; B-LC10: LC10 of beta-cypermethrin; BLC30: LC30 of beta-cypermethrin; I-LC10: LC10 of indoxacarb; I-LC30: LC30 of indoxacarb.

Table 1. Toxicity of beta-cypermethrin and indoxacarb to apterous
adults of Rhopalosiphum padi.

Insecticide     n    Slope [+ or -]    [chi     df     Concentration
               (a)         SE         square]         (95% CI) (mg/L)

Beta-          658   2.06 [+ or -]     2.13      3      LC10 = 0.39
cypermethrin              0.17                          (0.32-0.46)

                                                        LC30 = 0.92

Indoxacarb     616   1.64 [+ or -]     0.36      3      LC10 = 0.14
                          0.18                          (0.07-0.24)

                                                        LC30 = 0.42

(a) Number of apterous adult aphids tested.

Table 2. Effect of exposure of parent adults (F0 generation) of
Rhopalosiphum padi to beta-cypermethrin (B) and indoxacarb (I) at
LC10 and LC30 on their fecundity and longevity (mean [+ or -] SE).

Treatment    Adult longevity (d)    Number of offspring per

Control      19.33 [+ or -] 1.13a    51.57 [+ or -] 3.16a
B-LC10       9.52 [+ or -] 1.50bc    17.17 [+ or -] 3.17bc
B-LC30       6.00 [+ or -] 1.54c     12.03 [+ or -] 3.47c
I-LC10       13.40 [+ or -] 1.09b    26.97 [+ or -] 2.41b
I-LC30       11.48 [+ or -] 1.50b    23.57 [+ or -] 3.42bc

Data followed by the same lower case letter in the same
column were not significantly different based on Tukey's
tests (P > 0.05).

Table 3. Effect of exposure of parent adults of Rhopalosiphum padi to
beta-cypermethrin (B) and indoxacarb (I) at LC10 and LC30 on
fecundity and longevity (mean [+ or -] SE) of the F1 generation
of R. padi.

Treatment        Life span (d)        Number of offspring
                                          per female

Control      25.16 [+ or -] 0.93ab   55.88 [+ or -] 3.41a
B-LC10       23.28 [+ or -] 1.39ab   46.37 [+ or -] 2.24ab
B-LC30       20.57 [+ or -] 1.64b    37.13 [+ or -] 2.93b
I-LC10       25.76 [+ or -] 0.89a    48.96 [+ or -] 3.40a
I-LC30       23.73 [+ or -] 1.13ab   48.86 [+ or -] 3.85a

Data followed by the same lower case letter in the same column were
not significantly different based on Tukey's tests (P > 0.05).

Table 4. Effect of exposure of parent adults of Rhopalosiphum padi to
beta-cypermethrin (B) and indoxacarb (I) at LC10 and LC30 on various
population parameters (mean [+ or -] SE) of the F1 generation
of R. padi.

                  Intrinsic rate
                 of increase (r)
Treatment          ([d.sup.-1])

Control      0.4235 [+ or -] 0.0053a
B-LC10       0.3593 [+ or -] 0.0083c
B-LC30       0.3517 [+ or -] 0.0094c
I-LC10       0.3994 [+ or -] 0.0050ab
I-LC30       0.3883 [+ or -] 0.0070b

                  Finite rate            Net reproduction
                  of increase             rate [R.sub.0]
Treatment          ([lambda])             (offspring per
                  ([d.sup.-1])             individual)

Control      1.527 [+ or -] 0.0081a   55.88 [+ or -] 2.280a
B-LC10       1.432 [+ or -] 0.0001c   41.82 [+ or -] 2.759bc
B-LC30       1.422 [+ or -] 0.0133c   33.42 [+ or -] 3.031c
I-LC10       1.491 [+ or -] 0.0074b   54.44 [+ or -] 2.158a
I-LC30       1.474 [+ or -] 0.0103b   48.96 [+ or -] 2.579ab

                Mean generation        Gross reproduction
                    time (T)          rate GRR (offspring
Treatment         ([d.sup.-1])          per individual)

Control       9.51 [+ or -] 0.103b    61.37 [+ or -] 1.10a
B-LC10       10.39 [+ or -] 0.165a    53.76 [+ or -] 1.02b
B-LC30       9.98 [+ or -] 0.158ab    51.03 [+ or -] 1.35b
I-LC10       10.01 [+ or -] 0.096ab   59.45 [+ or -] 0.95a
I-LC30       10.02 [+ or -] 0.195ab   59.57 [+ or -] 1.04a

Data followed by the same lower case letter in the same
column were not significantly different based on Tukey's tests
(P > 0.05).


Please note: Some tables or figures were omitted from this article.
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Article Details
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Author:Zuo, Yayun; Wang, Kang; Lin, Fangfei; Li, Yuting; Peng, Xiong; Pinero, Jaime C.; Chen, Maohua
Publication:Florida Entomologist
Article Type:Report
Geographic Code:1U5FL
Date:Sep 1, 2016
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