Chemical group, active ingredient and mechanism of action of the insecticides used in sublethal effects studies presented in this chapter.
Abstract
Studies related to the effect of insecticides on insect pests and nontarget organisms, such as natural enemies, are traditionally accessed by the estimative of lethal effects, through mortality data. Due to the limitations of the traditional methods, recent studies in the past three decades are assessing the sublethal effects of insecticides upon several important biological traits of insect pests and natural enemies. Besides mortality, the sublethal dose/concentrations of an insecticide can affect insect biology, physiology, behavior and demographic parameters. In this chapter, many sublethal effects of insecticides were addressed for several chemical groups, such as botanical insecticides, carbamate, diamide, insect growth regulators, neonicotinoid, organochlorides, organophosphates, pyrethroid and others. An accurate assessment of these effects is crucial to acquire knowledge on the overall insecticide efficacy in the management of pest insect populations, as well as on their selectivity toward nontarget organisms.
Keywords
- sublethal concentrations
- pest insects
- natural enemies
- biological effects
- physiological effects
- behavioral effects
- demographic studies
1. Introduction
Despite numerous novel control agents available at integrated pest management programs, insecticides remain as the most reliable method for insect control. The effects of insecticides and other toxicants on insect pests and other arthropods have been the subject of innumerous studies in the past several decades [1]. Methods to test the side effects of toxicants have been developed as a function of insect control evaluations. For a long time, the classical laboratory method for estimating the side effects of insecticides on insect pests, natural enemies and beneficial arthropods was to determine the median lethal dose (LD50) or lethal concentration (LC50) [2]. The assessment of lethal dose/concentrations is a very useful tool to compare the toxicities of different active ingredients and different formulations of insecticides containing the same active ingredient. The lethal estimates may also be an important information when evaluating the development of resistant pest populations to insecticides.
Although the results of such estimates in laboratory have been extremely valuable, interpretation of the data is severely limited. In field crops, lower insecticide dose/concentrations usually occur after the initial application, as they degrade by several abiotic factors, such as rainfall, temperature and sunlight. In this way, under field conditions, insects can be exposed to sublethal doses/concentrations of insecticides and may experience related to sublethal effects [3].
Sublethal effects are defined as biological, physiological, demographic or behavioral effects on individuals or populations that survive exposure to a toxicant at lethal or sublethal dose/concentration. A sublethal dose/concentration is defined as inducing no apparent mortality in the experimental population [2]. In general, insecticide dose/concentrations under the median lethal (LD50/LC50) are considered to be sublethal. The sublethal effects may be manifested as reductions in life span, development rates, population growth, fertility, fecundity, changes in sex ratio, deformities, changes in behavior, feeding, searching and oviposition [4, 5]. Thus, toxicants can exert subtle as well as overt effects that must be considered when examining their total impact.
Due to the recognition of limitations associated with traditional methods for studying sublethal effects, a growing body of the literature has aimed at assessing insecticide sublethal effects on various important biological traits of pests in the past three decades. An accurate assessment of these effects is crucial to acquire knowledge on the overall insecticide efficacy in the management of pest insect populations, as well as on their selectivity toward nontarget organisms, such as natural enemies [6].
Sublethal effects were reported in several insect orders upon different biological, physiological, behavioral and demographic aspects, such as the effect of the aqueous extract of
Among the insecticides used in sublethal effect studies, the botanical and biological insecticides, organochlorides, organophosphates, carbamates, diamides, hydrazines, growth regulators, neonicotinoids and pyrethroids demonstrate several adverse effects presented throughout this chapter (Table 1). Therefore, we aim to discuss the importance of sublethal effects of insecticides for integrated pest management programs, through the effects upon pest insect biology, physiology, behavior, demographic parameters and natural enemies.
Chemical group | Active ingredient | Mechanism of action |
---|---|---|
Spinosad | Nicotinic acetylcholine receptors and y‐aminobutyric acid receptors | |
Azadirachtin | Ecdysis inhibitor | |
Essential oils and major compounds in general | Ecdysis inhibitor, acetylcholinesterase inhibitor, octopamine mimic | |
Methomyl | Acetylcholinesterase inhibitors | |
Bisacylhydrazine (RH 5849) | Ecdysteroids agonists | |
Methoxyfenozide | ||
Tebufenozide | ||
Cyantraniliprole | Ryanodine receptors (affecting calcium channels in the sarcoplasmic reticulum) | |
Chlorantraniliprole | ||
Pyriproxyfen | Inhibition of the development of insect adult characteristics | |
Hexaflumuron | Chitin synthesis inhibitor | |
Lufenuron | ||
Novaluron | ||
Triflumuron | ||
Buprofezin | ||
Acetamiprid | Acetylcholine mimic | |
Clothianidin | ||
Imidacloprid | ||
Thiacloprid | ||
Endosulfan | Interfere with the transmission of nervous impulses (flux of Na and K) | |
Chlorpyrifos | Acetylcholinesterase inhibitors | |
Deltamethrin | Channel sodium modulators |
2. Sublethal effects upon insect biology
The effects of insecticides sublethal doses/concentrations upon insect biology may present itself through reduced oviposition, increased development period of immature stages or decreased life span. Nevertheless, the effect of sublethal doses/concentrations of some neurotoxic insecticides upon insect fecundity and fertility may be related to behavioral changes, particularly during their reproductive stage [11]. Several biological effects are reported in the literature due to the use of sublethal dose/concentrations of insecticides, for example, the sublethal effects of the insecticides lufenuron, methoxyfenozide, spinosad, endosulfan, novaluron and tebufenozide upon
Several studies also report the sublethal effects of essential oils and their compounds upon insect biology. The insecticidal activity of essential oils is based on the high concentrations of major compounds that belong to the classes of terpenes, phenolics and alkaloids [15]. The essential oils of long pepper and clove demonstrated the activity of these substances on several biological parameters of
The assessment of the sublethal effects of insecticides upon insect biology is of great importance for the integrated pest management programs, as sublethal doses/concentrations do not cause the insect death, but through the interference in biological traits may reduce the insect populations of next generations in the crops.
3. Insect behavior as a measurement of insecticide sublethal effects
The exposure to insecticide sublethal dose/concentrations may cause changes in several behavioral parameters of insects, such as food foraging, choice of oviposition sites, pheromonal communications and others. The production and emission of pheromone by females, males and its detection depend on complex physiological mechanisms involving hormones and neurohormones. Some insecticides that act on the endocrine system may also influence reproductive behavior.
Sublethal dose/concentrations of insecticides may change the chemical communication system and, therefore, decrease chances of reproduction in insects that largely rely on olfactory communication. For example, the effects of deltamethrin on the calling behavior and production of sex pheromone in
Besides adverse effects, the insecticides at sublethal doses/concentrations may cause positive responses at reproduction, known as hormesis and hormoligosis. However, there is still little information regarding the effects of sublethal dose/concentrations on insect behavior [21]. The sublethal doses of clothianidin on males of
Sublethal doses of deltamethrin on
The sublethal dose LD01 of chlorpyrifos on
Altering plants‐specific odor bouquet by nonspecific odors may cause oviposition sites rejection. In this way, insecticide sublethal doses/concentrations may present deterrent effect for insect oviposition and feeding. Sublethal concentrations of several essential oils caused the reduction in feeding and oviposition of
The use of behavioral control together with chemical control in the integrated pest management is recognized as a promising and efficient tool. For that, the evaluation of sublethal effects of insecticides in insect behavior is essential for the development of new strategies.
4. Physiological responses to insecticides sublethal doses/concentrations
Exposure to sublethal doses/concentrations of insecticides that attack the nervous system or disrupt the hormonal balance can affect insect physiology and reduce survival and reproduction [29]. Potentially, all classes of insecticides can affect insect reproduction through sublethal adverse effects on physiological parameters, such as egg fertilization, oogenesis, ovulation, spermatogenesis and sperm motility [11].
Insect growth regulators (IGRs) are ecdysone agonists and specific for Lepidoptera larvae, being effective against many important crop pests [30]. The HR 5849 bisacylhydrazine and the tebufenozide (RH‐5992) IGRs insecticides adversely affect the development of male reproductive system and testicular volume of
Studies with neonicotinoids, which act as agonist of acetylcholine receptor and disturb the neuronal cholinergic signal transduction, demonstrate that thiacloprid, imidacloprid and clothianidin can also interfere with the immune system of honeybees, affecting the total number of hemocytes, the encapsulation response and microbial activity in the hemolymph [32]. Besides effects on the immune system, neonicotinoids such as imidacloprid have been found to reduce sperm viability by 50% in bees [33]. These factors may also affect disease resistance capacity [34].
Insecticides from the anthranilamide class, such as ciantraniliprole, target the rianodiana receptors in the muscles and the calcium channels [35, 36]. Ciantraniliprole demonstrated sublethal effects upon
The amylase activity in the midgut of
Natural insecticides also demonstrate sublethal effects in physiological parameters of insects.
Other physiological parameters such as spermatogenesis and ovarioles histochemistry of
Understanding the physiological processes that affect insect life traits is an important step for the evaluation of the overall insecticide effects upon insect pest and natural enemies in integrated pest management programs.
5. Demographic studies for the assessment of insecticide sublethal effects
The use of ecotoxicology approaches is improving the evaluation of insecticides and other toxicants in integrated pest population control programs. The traditional lethal dose/concentration estimates are designed to measure one effect at a time [1]. Demography studies derive better estimates of insecticides impacts on insect pests and natural enemies, since it accounts for all effects a toxicant might have on a population including interactions that are not perceptible in short‐term toxicity [47, 48].
The analysis of demographic parameters can evaluate sublethal effects well below the traditional dose/concentration‐response curve, resulting in the assessment of population decline and extinction at doses/concentrations previously assumed to have few effects on individuals [49]. On the other hand, sublethal doses/concentrations of insecticides may also result in pest populations outbreaks mediated by reproduction stimulation [50, 51].
Demographic toxicological studies through fertility life table bioassays provide a measure of the insecticide effect upon the population growth rate. The sublethal effects on population growth rate after exposure to insecticides are highly influenced by the starting population structure. Because different insect stages/ages may present different susceptibilities to toxicants, it is essential to consider this factor to estimate the population susceptibility [52].
Life table response experiments are conducted by exposing individuals or groups to increasing doses or concentrations of a toxicant over their life span. Daily mortality and reproduction are recorded and used to generate life table parameters [1]. In the fertility life table study, the intrinsic rate of increase (
The instantaneous rate of increase is calculated by the following equation:
These demographic approaches have been used in a toxicological context by several authors to assess the sublethal effects of synthetic. The use of fertility life table bioassays demonstrated that sublethal concentrations of cyantraniliprole decreased growth speed and reduced population reproduction of
In this way, the study of sublethal effects of insecticides on insect pests and natural enemies through the use of demographic parameters is crucial for guiding the use of new toxicants, delaying the development of resistance and reducing the risk of pest resurgence.
6. Sublethal effects of insecticides on biological control
The studies of insecticide effects on beneficial insects, particularly natural enemies, have grown in recent years. These impacts are not limited to mortality, as they also present sublethal effects on insects that survive the insecticide exposure [2]. These effects may result, for example, in changes of biological parameters, reproduction (fertility, fecundity and sex ratio), development time, longevity and insect behavior [11, 63].
The sublethal effects upon natural enemies can be divided in two groups: physiological and behavioral. Among the physiological effects are changes in neurophysiology, development, adult longevity, fecundity and sex ratio [2]. Among the behavioral effects upon natural enemies are the changes in mobility of insects, although it is still little studied, changes in the ability to search for prey or host and changes in feeding behavior and insect oviposition.
Insect growth regulators (IGRs) may promote changes in the development of natural enemies by the interruption of the molting process and cuticle formation, besides acting upon the endocrine system of insects [2]. Fecundity and fertility reduction were observed as sublethal effects of insect growth regulators on the predator larvae of
Not only synthetic insecticides are likely to affect the natural enemies but also botanical insecticides and essential oils. The effect of the neem‐based botanical insecticide Azamax®, the aqueous extract of neem and the emulsifiable oil of
Sublethal doses/concentrations of insecticides can also affect beneficial insects such as bees, causing changes in development, behavior, morphophysiology and immune system, affecting the colony functions and decreasing the longevity of individuals [72]. The assessment of selective insecticides to natural enemies is of utmost importance for biological control on integrated management programs.
7. Conclusion
Studies on sublethal effects have been quite elucidated over the last decade, for synthetic and botanical insecticides effects upon pest insects and natural enemies (parasitoids and predators). However, this is still the beginning of the path of knowledge for this particularly area, since each individual and species may present a different response to each insecticide.
Overall, sublethal effects of insecticides may cause biological effects, disturbing the number of eggs, oviposition period, larval and pupal weight, development period, adult emergency, longevity and fertility; behavioral effects on feeding, oviposition, locomotor system and reducing or increasing the production and response to pheromones; and physiological effects upon reproductive and immune systems as well as upon the nutritional status of insects.
The use of demographic parameters in the assessment of sublethal effects came to extend the concept of the total effect of insecticides not only upon individuals, but also on insect populations. In addition, the assessment of sublethal effects upon natural enemies enables the development of integrated pest management programs with safer and effective combined use of chemical and biological control.
For future works, it is also important to target a broader look and observe the effect of sublethal doses/concentrations upon insects life history and expand this impact to a more widely perspective, such as communities and the ecosystem. The study of sublethal effects of insecticides upon insects is of great importance and need to be considered when accessing the total effect of a toxicant.
References
- 1.
Stark JD, Banks JE. Population‐level effects of pesticides and other toxicants on arthropods. Annual Review of Entomology. 2003; 48: 505–519. doi:10.1146/annurev.ento.48.091801.112621 - 2.
Desneux N, Decourtye A, Delpuech JM. The sublethal effects of pesticides on beneficial arthropods. Annual Review Entomology. 2007; 52: 81–106. doi:10.1146/annurev.ento.52.110405.091440 - 3.
Stark JD, Jepson PC, Mayer D. Limitations to the use of topical toxicity data for predictions of pesticide sideeffects in the field. Journal of Economic Entomology. 1995; 88(5):1081–1088. doi:10.1093/jee/88.5.1081 - 4.
Lee CY. Sublethal effects of insecticide on longevity, fecundity, and behaviour of insect pests: a review. Bioscience Journal. 2000; 11: 107–112. http://www.chowyang.com/uploads/2/4/3/5/24359966/034.pdf - 5.
Singh JP, Marwaha KK. Effects of sublethal concentrations of some insecticides on growth and development of maize stalk borer, Chilo partellus (Swinhoe) larvae. Shashpa. 2000; 7: 181–186. - 6.
Biondi A, Mommaerts V, Smagghe G, Viñuela E, Zappalà L, Desneux N. The non‐target impact of spinosyns on beneficial arthropods. Pest Management Science. 2012; 68: 1523–1536. doi:10.1002/ps.3396 - 7.
Borgoni PC, Vendramin JD. Sublethal effect of aqueous extracts of Trichilia spp. on Spodoptera frugiperda (J.E. Smith) (Lepidoptera: Noctuidae) development on maize. Neotropical Entomology. 2005; 34: 311–317. doi:10.1590/S1519‐566X2005000200020 - 8.
Mamood AN, Waller GD. Recovery of learning responses by honeybees following sublethal exposure to permethrin. Physiological Entomology. 1990; 15: 55–60. doi:10.1111/j.1365‐3032.1990.tb00492.x - 9.
Lashkari MA, Sahragard A, Ghadamyari M. Sublethal effects of imidacloprid and pymetrozine on population growth parameters of cabbage aphid, Brevicoryne brassicae on rapeseed,Brassica napus L. Insect Science. 2007; 14: 207–212. doi:10.1111/j.1744‐7917.2007.00145.x - 10.
Elzen GW, Maldonado SN, Rojas MG. Lethal and sublethal effects of selected insecticides and an insect growth regulator on the boll weevil (Coleoptera: Curculionidae) ectoparasitoid Catolaccus grandis (Hymenoptera: Pteromalidae). Journal of Economic Entomology. 2000; 93: 300–303. doi:10.1603/0022‐0493‐93.2.300 - 11.
Haynes KF. Sublethal effects of neurotoxic insecticides on insect behavior. Annual Review Entomology. 1988; 33: 149–168. doi:10.1146/annurev.en.33.010188.001053 - 12.
Storch G, Loeck AE, Borba RS, Magano DA, Moraes CL, Grutzmacher CL. The effect of sub-lethal do.ses of insecticides on artificial diet and caterpillars of Anticarsia gemmatalis (Lepidoptera: Noctuidae). Revista Brasileira de Agrociência. 2007; 13: 175–179. doi:10.18539/CAST.V13I2.1358 - 13.
Mahmoudvand M, Abbasipour H, Garjan AS, Bandani AR. Decrease in pupation and adult emergence of Plutella xylostella (L.) treated with hexaflumuron. Chilean Journal of Agricultural Research. 2012; 72: 206–211. doi:10.4067/S0718‐58392012000200007 - 14.
Dong J, Wang K, Li Y, Wang S. Lethal and sublethal effects of cyantraniliprole on Helicoverpa assulta (Lepidoptera: Noctuidae). Pesticide Biochemistry and Physiology. 2016. doi:10.1016/j.pestbp.2016.08.003 - 15.
Ootani MA, Aguiar RW, Ramos ACC, Brito DR, Silva JB, Cajazeira JP. Use of essential oils in agriculture. Journal of Biotechnology and Biodiversity. 2013; 4: 162–174. - 16.
Cruz GS, Wanderley‐Teixeira V, Oliveira JV, Correia AA, Breda MO, Alves TJS, Cunha FM, Teixeira AAC, Dutra KA, Navarro DMAF. Bioactivity of Piper hispidinervum (Piperales: Piperaceae) andSyzygium aromaticum (Myrtales: Myrtaceae) olis, with or without formulated Bta on the biology and immunology ofSpodoptera frugiperda (Lepidoptera: Noctuidae). Journal of Economic Entomology. 2014; 107: 144–153. doi:10.1603/EC13351 - 17.
Cruz GS, Wanderley‐Teixeira V, Oliveira JV, Lopes FSC, Barbosa DRS, Breda MO, Dutra KA, Guedes CA, Navarro DMAF, Teixeira ACC. Sublethal effects of essential oils from Eucalyptus staigeriana (Myrtales: Myrtaceae),Ocimum gratissimum (Lamiales: Laminaceae), andFoeniculum vulgare (Apiales: Apiaceae) on the biology ofSpodoptera frugiperda (Lepidoptera: Noctuidae). Journal of Economic Entomology. 2016; 109: 660–666. doi:10.1093/jee/tow005 - 18.
Bernardi D, Oabne S, Bernardi O, Silva A, Cunha US, Garcia MS. Efficiency and sublethal effects of neem on Bonagota salubricola (Meyrick) (Lepidoptera: Tortricidae). Revista Brasileira de Fruticultura. 2011; 33: 412–419. doi:10.1590/S0100‐2945201100500 0076 - 19.
De‐Ling MA, Gordh G, Zalucki MP. Biological effects of azadirachtin on Helicoverpa armigera (Hübner) (Lepidoptera:Noctuidae) fed on cotton and artificial diet. Australian Journal of Entomology. 2000; 39: 301–304. doi:10.1046/j.1440‐6055.2000.00180.x - 20.
Wei H‐Y, Du J‐W. Sublethal effects of larval treatment with deltamethrin on moth sex pheromone communication system of the Asian corn borer Ostrinia furnacalis . Pesticide Biochemistry and Physiology. 2004; 80: 12–30. doi:10.1016/j.pestbp.2004.05.001 - 21.
Cutler GC. Insects, insecticides and hormesis: evidence and considerations for study. Dose Response. 2013; 11: 154–117. doi:10.2203/dose‐response.12‐008.Cutler - 22.
Rabhi KK, Esancy K, Voisin A, Crespin L, Le Corre J, Tricoire‐Leignel H, Anton S, Gadenne C. Unexpected effects of low doses of a neonicotinoid insecticide on behavioral responses to sex pheromone in a pest insect. PLoS One. 2012; 9(12): e114411. doi:10.1371/journal.pone.0114411 - 23.
Lalouette L, Pottier M, Wycke M, Boitard C, Bozzolan F, Maria A, Demondion E, Chertemps T, Lucas P, Renault D, Maibeche M, Siaussat D. Unexpected effects of sublethal doses of insecticide on the peripheral olfactory response and sexual behavior in a pest insect. Environmental Science and Pollution Research. 2016; 23: 3073–3085. doi:10.1007/s11356‐015‐5923‐3 - 24.
Delpuech J, Gareau E, Terrier O, Fouillet P. Sublethal effects of the insecticide chlorpyrifos on ti‐ijz sex pheromonal communication of Trichogramma brassicae. Chemosphere. 1998; 36: 1775–1785. doi:10.1016/s0045‐6535(97)10071‐6 - 25.
Delpuech J, Delahaye M. The sublethal effects of deltamethrin on Trichogramma behaviors during the exploitation of host patches. Science of the Total Environment. 2013; 447C: 274–279. - 26.
Ribeiro CR, Zanuncio TV, Ramalho FS, Silva CAD, Serrão JE, Zanuncio JC. Feeding and oviposition of Anticarsia gemmatalis (Lepidoptera: Noctuidae) with sublethal concentrations of ten condiments essential oils. Industrial Crops and Products. 2015; 74: 139–143. doi:10.1016/j.indcrop.2015.03.057 - 27.
Dewer Y, Pottier M, Lalouette L, Maria A, Dacher M, Belzunces LP, Kairo G, Renault D, Maibeche M, Siaussa D. Behavioral and metabolic effects of sublethal doses of two insecticides, chlorpyrifos and methomyl, in the Egyptian cotton leafworm, Spodoptera littoralis (Boisduval) (Lepidoptera: Noctuidae). Environmental Science and Pollution Research. 2016; 23: 3086–3096. doi:10.1007/s11356‐015‐5710‐1 - 28.
Haddi K, Oliveira EE, Faroni LRA, Guedes DC, Miranda NNS. Sublethal exposure to clove and cinnamon essential oils induces hormetic‐like responses and disturbs behavioral and respiratory responses in Sitophilus zeamais (Coleoptera: Curculionidae). Journal of Economic Entomology. 2015; 108: 2815–2822. doi:10.1093/jee/tov255 - 29.
Guedes RNC, Smagghe G, Stark JD, Desneux N. Pesticide‐induced stress in arthropod pests for optimized integrated pest management programs. Annual Review Entomology. 2016; 61: 43–62. doi:10.1146/annurev‐ento‐010715‐023646 - 30.
Cadogan BL, Retnakaran A, Meating JH. Efficacy of RH‐5992, a new insect growth regulator against spruce budworm (Lepidoptera: Torticidade) in a boreal forest. Journal Economic Entomology. 1997; 90: 551–559. doi:10.1093/jee/90.2.551 - 31.
Seth RK, Kaur JJ, Rao DK, Reynolds SE. Effects of larval exposure to sublethal concentrations of the ecdysteroid agonists RH‐5849 and tebufenozide (RH‐5992) on male reproductive physiology in Spodoptera litura. Journal of Insect Physiology. 2004; 50: 505–517. doi:10.1016/j.jinsphys.2004.03.007 - 32.
Elbert A, Hass M, Springer B, Thielert W, Nauen R. Applied aspects of neonicotinoid uses in crop protection. Pest Management Science. 2008; 64: 1099–1105. doi:10.1002/ ps.1616 - 33.
Chaimanee V, Evans JD, Chen Y, Jackson C, Pettis JS. Sperm viability and gene epression in honey bee ueens ( Apis mellifera ) folloing exposure to the neonicotinoid insecticide imidacloprid and the organophosphate acaricide coumaphos. Journal Insect Physiology. 2016; 89: 1–8. doi:10.1016/j.jinsphys.2016.03.004 - 34.
Brandt A, Gorenflo A, Siede R, Meiner M, Buchler R. The neonicotinoids thiacloprid, imidacloprid, and clothianidin affect the immunocompetence of honey bees ( Apis mellifera L.). Journal Insect Physiology. 2016; 86: 40–47. doi:10.1016/j.jinsphys.2016.01.001 - 35.
Sattelle DB, Cordova D, Cheek TR. Insect ryanodine receptors: molecular targets for novel pest control chemicals. Invertebrate Neuroscience. 2008; 8: 107–119. doi:10.1007/s10158‐008‐0076‐4 - 36.
Lahm GP, Cordova D, Barry JD. New and selective ryanodine receptor activators for insect control. Bioorganic and Medicinal Chemistry. 2009; 17: 4127–4133. doi:10.1016/j.bmc.2009.01.018 - 37.
Xu C, Zhang Z, Cui K, Zhao Y, Han J, Liu F, Mu W. Effects of sublethal concentrations of cyantraniliprole on the development, fecundity and nutritional physiology of the black cutworm Agrotis ipsilon (Lepidoptera: Noctuidae). PLoS One. 2016; 11(6): e0156555. doi:10.1371/journal.pone.0156555 - 38.
Hui‐Ling Y, Xin X, Gui‐in Y, Yi‐Qu C, Xue‐Gui W. Effects of sublethal doses of cyantraniliprole on the growth and development and the activities of detoxifying enzymes in Spodoptera exigua (Lepidoptera: Noctuidae). Acta Entomologica Sinica. 2015; 58: 634–641. http://www.insect.org.cn/EN/Y2015/V58/I6/634 - 39.
Saleem MA, Shakoori AR. Point effects of Dimilin and Ambush on enzyme activies of Tribolium castaneum larvae. Pesticide Biochemistry and Physiology. 1987; 29: 127–137. - 40.
Dewer Y, Pottier MA, Lalouette L, Maria A, Dacher M, Belzunces LP, Kairo G, Renault D, Maibeche M, Siaussat D. Behavioral and metabolic effects of sublethal doses of two insecticides, chlorpyrifos and methomyl, in the Egyptian cotton leafworm, Spodoptera littoralis (Boisduval) (Lepidoptera: Noctuidae). Environmental Science & Pollution Research International. 2016; 23: 3086–3096. doi:10.1007/s11356‐015‐5710‐1 - 41.
Shekari M, Sendi JJ, Etebari K, Zibaee A, Shadparvar A. Effects of Artemisia annua L. (Asteracea) on nutritional physiology and enzyme activities of elm leaf beetle,Xanthogaleruca luteola Mull (Coleoptera: Chrysomelidae). Pesticide Biochemistry and Physiology. 2008; 91: 66–74. doi:10.1016/j.pestbp.2008.01.003 - 42.
Zamari S, Sendi JJ, Ghadamyari M. Effect of Artemisia annua L. (Asterales: Asteraceae) essential oil on mortality, development, reproduction and energy reserves ofPlodia interpunctella (Hubner) (Lepidoptera: Pyralidae). Journal of Fertilizers and Pestcidies. 2011; 2: 105–110. doi:10.4172/2155‐6202.1000105 - 43.
Correia AA, Wanderley‐Teixeira V, Teixeira AAC, Oliveira JV, Gonçalves GG, Cavalcanti MG, Brayner FA, Alves LC. Microscopic analysis of Spodoptera frugiperda (Lepidoptera: Noctuidae) embryonic development before and after treatment with azadirachtin, lufenuron, and deltamethrin. Journal Economic Entomology. 2011; 106: 747–755. doi:10.1603/EC12158 - 44.
Alves TJS, Cruz GS, Wanderley‐Teixeira V, Teixeira AAC, Oliveira JV, Correia AA, Câmara AAG, Cunha FM. Effects of Piper hispidinervum on spermatogenesis and histochemistry of ovarioles ofSpodoptera frugiperda. Biotechnic and Histochemistry. 2013; 88: 1–11. doi:10.3109/10520295.2013.837509 - 45.
Cruz GS, Teixeira VW, Oliveira JV, Teixeira AAC, Araújo AC, Alves TJS, Cunha FM, Breda MO. Histological and histochemical changes by clove essential oil upon the gonads of Spodoptera frugiperda (J.E. Smith) (Lepidoptera: Noctuidae). International Journal of Morphology. 2015; 33: 1393–1400. doi:10.4067/S0717‐95022015000400034 - 46.
Silva CTS, Wanderley‐Teixeira V, Cunha FM, Oliveira JV, Dutra KA, Navarro DMAF, Teixeira AAC. Biochemical parameters of Spodoptera frugiperda (J. E. Smith, 1979) treated with citronella oil (Cymbopogon wintwrianus Jowitt ex Bor) and its influence on reproduction. Acta Histochemistry. 2016; 118: 347–352. - 47.
Kammenga JE, Busschers M, Van Straalen NM, Jepson JP, Bakker J. Stress‐induced fitness reduction is not determined by the most sensitive lifecycle trait. Functional Ecology. 1996; 10: 106–111. doi:10.2307/2390268 - 48.
Kareiva P, Stark J, Wennergren U. Using demographic theory, community ecology and spatial models to illuminate ecotoxicology. In: Baird DJ, Maltby L, Greig‐Smith PW, Douben PET (eds.), Ecotoxicology: Ecological Dimensions. London: Chapman & Hall; 1996. pp. 13–23. doi:10.1007/978‐94‐009‐1541‐1_3 - 49.
Bechmann RK. Use of life tables and LC50 tests to evaluate chronic and acute toxicity effects of copper on the marine copepod Tisbe furcata (Baird). Environmental Toxicology and Chemistry. 1994; 13: 1509–1517. doi:10.1002/etc.5620130913 - 50.
Kerns DL, Gaylor MJ. Sublethal effects of insecticides on cotton aphid reproduction and color morph development. Southwestern Entomologist. 1992; 17: 245–250. - 51.
Kerns DL, Gaylor MJ. Induction of cotton aphid outbreaks by insecticides in cotton. Crop Protection. 1993; 12: 387–392. doi:10.1016/0261‐2194(93)90083‐U - 52.
Stark JD, Banken JAO. Importance of population structure at the time of toxicant exposure. Ecotoxicology and Environmental Safety. 1999; 42: 282–287. doi:10.1006/eesa.1998.1760 - 53.
Huang YB, Chi H. Life tables of Bactrocera cucurbitae (Diptera: Tephritidae): with an invalidation of the jackknife technique. Journal of Applied Entomology. 2013; 137: 327–339. doi:10.1111/jen.12002 - 54.
Stark JD, Banks JE. Developing demographic toxicity data: optimizing effort for predicting population outcomes. PeerJ. 2016; 4: e2067. doi:10.7717/peerj.2067 - 55.
Banken JAO, Stark JD. Multiple routes of pesticide exposure and the risk of pesticides to biological controls: a study of neem and the seven‐spot lady beetle, Coccinella septempunctata L. Jounal of Economic Entomology. 1998; 91: 1–6. doi:10.1093/jee/91.1.1 - 56.
Han W, Zhang S, Shen F, Liu M, Ren C, Gao X. Residual toxicity and sublethal effects of chlorantraniliprole on Plutella xylostella (Lepidoptera: Plutellidae). Pest Management Science. 2012; 68: 1184–1190. doi:10.1002/ps.3282 - 57.
Song Y, Dong J, Sun H. Chlorantraniliprole at sublethal concentrations may reduce the population growth of the Asian corn borer, Ostrinia furnacalis (Lepidoptera: Pyralidae). Acta Entomologica Sinica. 2013; 56: 446–451. - 58.
Yin XH, Wu QJ, Li XF, Zhang YJ, Xu BY. Demographic changes in multigeneration Plutella xylostella (Lepidoptera: Plutellidae) after exposure to sublethal concentrations of spinosad. Journal of Economic Entomology. 2009; 102: 357–365. doi:10.1603/029. 102.0146 - 59.
Wang D, Wang YM, Liu HY, Xin Z, Xue M. Lethal and sublethal effects of spinosad on Spodoptera exigua (Lepidoptera: Noctuidae). Journal of Economic Entomology. 2013; 106: 1825–1831. doi:10.1603/EC12220 - 60.
Breda MO, Oliveira JV, Marques EM, Ferreira RG, Santana MF. Botanical insecticides applied on Aphis gossypii and its predatorCycloneda sanguinea on naturally colored cotton. Pesquisa Agropecuária Brasileira. 2011; 46: 1424–1431. doi:10.1590/S0100‐204X2 011001100002 - 61.
Andrade LH, Oliveira JV, Breda MO, Marques EJ, Lima IMM. Effects of botanical insecticides on the instantaneous population growth rate of Aphis gossypii Glover (Hemiptera: Aphididae) in cotton. Acta Scientiarum Agronomy. 2012; 34: 119–124. doi:10.4025/actasciagron.v34i2.10863 - 62.
Venzon M, Rosado MC, Pallini A, Fialho A, Pereira CJ. Lethal and sublethal toxicity of neem on green peach aphid and on its predator Eriopis conexa . Pesquisa Agropecuária Brasileira. 2007; 42: 627–631. doi:10.1590/S0100‐204X2007000500003 - 63.
Wright DJ, Verkerk RHJ. Integration of chemical and biological control systems for arthropods: evaluation in a multitrophic context. Pesticide Science. 1995; 44: 207–218. doi:10.1002/ps.2780440302/ - 64.
Ono EK. Lethal and sublethal effects of insect growth regulators over the predator Ceraeochrysa cubana (Hagen, 1861) (Neuroptera: Chrysopidae) under laboratory conditions. Dissertação de mestrado, Escola Superior de Agricultura “Luiz de Queiroz”, Piracicaba, SP, Brasil. 2014; 48 p. - 65.
Ohba SY, Ohashi K, Pujiyati E, Higa Y, Kawada H, Mito N, Takagi M. The effect of Pyiriproxyfen as a “population growth regulator” against Aedes albopictus under semi‐field conditions. PLoS One. 2013; 8: e67045. doi:10.1371/journal.pone.0067045 - 66.
Carvalho GA, Godoy MS, Parreira DS, Lasmar O, Souza JR, Moscardini VF. Selectivity of growth regulators and neonicotinoids for adults of Trichogramma pretiosum (Hymenoptera: Trichogrammatidae). Revista Colombiana de Entomología. 2010; 36: 195–201. - 67.
Rill SM, Grafton‐Cardwell EE, Morse JG. Effects of two insect growth regulators and a neonicotinoid on various life stages of Aphytis melinus (Hymenoptera: Aphelinidae). BioControl. 2008; 53: 579–587. doi:10.1007/s10526‐007‐9097‐x - 68.
Garzón A, Medina P, Amor F, Viñuela E, Budia F. Toxicity and sublethal effects of six insecticides to last instar larvae and adults of the biocontrol agents Chisoperla carnea (Stephens) (Neuroptera: Chrysopidae) andAdalia bipunctata (L.) (Coleoptera: Coccinellidae). Chemosphere. 2015; 132: 87–93. doi:10.1016/j.chemosphere.2015.03.016 - 69.
Fonseca APP, Marques EJ, Torres JB, Silva LM, Siqueira HAA. Lethal and sublethal effects of lufenuronon sugarcane borer Diatraea flavipennella and its parasitoidCotesia flavipes. Ecotoxicology. 2015; 24: 1869–1879. doi:10.1007/s10646‐015‐1523‐8 - 70.
Trindade RCP, Lima IS, Sant'Ana AEG, Broglio SMF, Silva PP. Ação de extratos vegetais sobre Trichogramma galloi (Zucchi, 1988) (Hymenoptera: Trichogrammatidae). Comunicata Scientiae. 2013; 4: 255–262. - 71.
Silva AB, Batista JL, Brito CH. Influência de produtos de origem vegetal na oviposição e no desenvolvimento embrionário de Euborellia annulipes (Dermaptera: Anisolabididae). Engenharia Ambiental. 2009; 6: 54–65. - 72.
Frazier M, Mullin C, Frazier J, Ashcraft S. What have pesticides got to do with it? American Bee Journal, Hamilton. 2008: 521–523. Available from: http://maarec.cas.psu. edu/CCDPpt/WhatPesticidesToDOWithltJune08ABJ.pdf