Insecticide Biochemistry and Physiology

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In the case of lipid reserves, fat concentrations in most of the tested tissues also appear not to be impacted by spinosyn as no changes in contents were observed. The exception to this was in forelimb muscles which showed a significant decrease in lipid levels in treated animals. Morphometric analyses, however, showed an increase in liver cell diameter, probably due to water accumulation promoting vacuolisation, which leads to cell hypertrophy.

Abnormal amounts of intracellular substances can be a manifestation of metabolic disturbances potentially leading to chronic cell injuries and even to cellular death.


This hydropic degeneration characterised by electrolyte and water accumulation inside hepatocytes is a non-lethal and very common injury that occurs as a response to several kinds of damage Pereira, Some few studies related to spinosyns-contamined mammals report small changes in the weight of some organs including liver, heart, kidneys and spleen. However, the dosages associated with these disturbances are not always applied in agriculture, which seems to indicate that low-dosage spinosyn does not seem to damage non target mammal.

Another important point is that rates of pesticide residues in the body began to decline after 14 days. So even when accumulated in the body, these compounds are at very low concentrations, which may be why no effects were observed in the energy metabolism of bats evaluated in our study. Overall, the spinosyns are readily subject to a number of diverse degradative pathways and metabolic mechanisms that reduce their persistence in plants, animals and the environment Kirst, To conclude, we demonstrate that spinosyn insecticides, as an alternative natural compound to classical insecticides, have little effect on glucose homeostasis or storage of energy in frugivorous bats A.

Further investigations are needed to confirm the lower risk of this class of pesticide for non-target organisms such as wild animals and to explore other factors associated with effects caused by this pesticide. We thank B. Freitas and Thomas C. Williams for revising the English version. Hyperglycemia associated with increased hepatic glycogen phosphorylase and phosphoenolpyruvate carboxykinase in rats following subchronic exposure to malathion.

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Food and Chemical Toxicology , vol. Toxic effects of spinosad on predatory insects. Biological Control , vol. Physical and biological properties of the spinosyns: Novel macrolide pest-control agents from fermentation. Phytochemicals for Pest Control. Washington: American Chemical Society.

Symposium Series, no. A simple method for the isolation and purification of total lipids from animal tissues.

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Journal of Biological Chemistry , vol. Seed dispersal by bats in a disturbed area of Southeastern Brazil. Revista de Biologia Tropical , vol. Evaluation of spinosad in a two generation dietary reproduction study using sprague-dawley rats. Toxicological Sciences , vol. The spinosyn family of insecticides: realizing the potencial of natural products research.

Journal of Antibiotics , vol. Discovery, isolation, and structure elucidation of a family of structurally unique, fermentation-derived tetracyclic macrolides. Energy reserves of Artibeus lituratus Chiroptera: Phyllostomidae in two areas with different degrees of conservation in Minas Gerais, Brazil. Brazilian Journal of Biology, vol. Saccharopolyspora spinosa sp. International Journal of Systematic Bacteriology , vol. DDT and metabolites residues in the southern bent-wing bat Miniopterus schreibersii bassanii of south-eastern Australia. Chemosphere , vol. The role of frugivorous bats in tropical forest succession.

Biological Reviews , vol. Regulation of glucose production by the liver. Annual Review of Nutrition , vol. B, E, H and K , thoracic ganglia control, 1, 12, 24 h treatments correspondingly. C, F, I and L , brain control, 1, 12, 24 h treatments correspondingly. Arrowheads indicate caspase-3 activity.

In the thoracic ganglia of the nymphs that were deltamethrin-exposed for 12 and 24 h, few regions showed nerve cells with a higher cleaved caspase-3 positive reaction Fig 5H and 5K. In the brain, no cleaved caspase-3 neurons were found for deltamethrin unexposed nymphs, whereas deltamethrin-exposed nymphs showed some cleaved caspase-3 positive neurons, but this was independent of the duration of deltamethrin exposure Fig 5C, 5F, 5I and 5L.

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DNA fragmentation was completely absent in the analysis of DNA integrity from the midgut, thoracic ganglia and brain of nymphs exposed to all time treatments, S2 Fig. The survival analysis of the data from C. Deltamethrin concentration higher than 0. A Survival curves of C. Only the survival curves of the highest concentrations 2. Points represent the censored data nymphs surviving until the end of the experiment, as well as the emerged adults.

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B Mean lifetime of C. Dispersion expressed as SE. The immature instars of benthic mayflies are among the most sensitive arthropods to pyrethroid insecticides [ 27 , 29 ]. Here, we assessed deltamethrin toxicity to C. The nymphs of C. Short-term up to 24 h and at 0. The cytomorphological alterations in the insect midgut caused by insecticides have been reported in different insect species [ 24 , 26 , 39 — 42 ]. Here, the degeneration of digestive cells e. The occurrence of detoxification processes in the insect midgut is not unexpected since the primary functions of the midgut include digestive enzyme production and nutrient absorption of digestion products [ 42 — 45 ].

In this sense, larvae of the mosquito Culex quinquefasciatus showed higher vacuolization in the midgut cells after exposure to insecticides, including deltamethrin [ 24 ]. It is worth to note that C. The presence of some cytoplasm basophilic granules in the midgut cells of 24 h deltamethrin-exposed nymphs suggest a potential bioaccumulation of deltamethrin and its byproducts, as suggested elsewhere for other toxicants [ 47 , 48 ].

One might suggest that the basophilic granules are nucleus fragments commonly found in cells that undergo apoptosis, but we showed by the Feulgen reaction that these granules are not of nuclear origin. In addition to the afore-mentioned changes, cytoplasm vacuolization in the midgut of C.

However, the measurements of cleaved caspase-3 positive cells, which are extensively used as an indicator of apoptosis in animal cells [ 54 — 56 ], only slightly increased in the midgut of deltamethrin-exposed nymphs.

Insecticide resistance in house flies from the United States

These cleaved caspase-3 cell increases might indicate an early stage of the apoptosis process in the assessed organs, but it cannot be ruled out that this phenomenon may be part of the normal cell renewal in these organs [ 56 , 57 ]. This latter hypothesis is supported by the absence of DNA fragmentation in the organs of C.

The brain and thoracic ganglia of C. Although major pyrethroid actions occur on the axonal nerve impulse transmission [ 17 — 19 ], here we found only slight changes in the cytomorphology of the nerve cells in the brain and in the thoracic ganglia. On contrary, the synganglion of the Rhipicephalus sanguineus Acari: Ixodidae females showed strong structural and enzymatic changes after exposure to the pyrethroid permethrin [ 59 ]. Such differential susceptibility might reflect differences between the protection efficacy provided by the perineurium and glial cells in insects and mites, once this cell layers prevent or decrease the interaction of insecticide molecules with the neural environment [ 59 — 61 ].

The differences of severity and type of cytomorphological changes among the organs studied may result from the deltamethrin toxicological characteristics. Deltamethrin also causes secondary effects that contribute to its toxicity [ 19 , 62 , 63 ]. For instance, osmotic imbalances in the digestive tract may contribute to deltamethrin secondary actions, since the digestive tract is one of the main routes of absorption and accumulation in heterotrophic aquatic organisms [ 64 , 65 ].

The survival of C. When exposed to sublethal concentrations of a pesticide, the basal metabolism of insects could increase in response to the physiological stress imposed by the pesticide [ 67 ], which might not affect the ability to survive a single insecticide pulse but will certainly increase the chance to make the insect less healthy [ 68 ].

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For instance, the sublethal exposure of arthropods to deltamethrin have been showed to impair their gas exchange system, decreasing the oxygen uptake and dysregulation of the breathing activities [ 69 ]. Thus, our findings show that the cytomorphological alterations found in the deltamethrin 0. We thank Dr. Jorge A. Dergam for allowing the use of the microscope imaging facilities, Dr.

Ana L. Salaro for providing free access to the fish-farming installations, Mr. Hemerson L. Freitas for his excellent technical assistance and the Center of Microscopy and Microanalyses from UFV for technical assistance. Browse Subject Areas? Click through the PLOS taxonomy to find articles in your field. Abstract Immature instars of mayflies are important constituents of the food web in aquatic ecosystems especially in Neotropical regions and they are among the most susceptible arthropods to pyrethroid insecticides.

Introduction The extensive use of pyrethroid insecticides in the control of virtually all agriculturally and medically important arthropod pests has raised concerns about its environmental safety, including their potential for serious harm in aquatic invertebrates [ 1 — 5 ]. Material and Methods All applicable international, national, and institutional guidelines for the care and use of animals were considered in the present investigation.

Insecticide Biochemistry and Physiology Insecticide Biochemistry and Physiology
Insecticide Biochemistry and Physiology Insecticide Biochemistry and Physiology
Insecticide Biochemistry and Physiology Insecticide Biochemistry and Physiology
Insecticide Biochemistry and Physiology Insecticide Biochemistry and Physiology
Insecticide Biochemistry and Physiology Insecticide Biochemistry and Physiology

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