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Search Results (187)

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Keywords = cypermethrin

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14 pages, 8730 KiB  
Article
Sublethal Effects of α-Cypermethrin on the Behavioral Asymmetries and Mating Success of Alphitobius diaperinus
by Demeter Lorentha S. Gidari, Nickolas G. Kavallieratos and Maria C. Boukouvala
Insects 2024, 15(10), 804; https://doi.org/10.3390/insects15100804 - 15 Oct 2024
Viewed by 419
Abstract
Sublethal exposure to insecticides can adversely impact various biological and behavioral characteristics of insects. Although α-cypermethrin has been previously tested for its effects on control of Alphitobius diaperinus, there is no knowledge about the effect of this insecticide on its behavioral asymmetries [...] Read more.
Sublethal exposure to insecticides can adversely impact various biological and behavioral characteristics of insects. Although α-cypermethrin has been previously tested for its effects on control of Alphitobius diaperinus, there is no knowledge about the effect of this insecticide on its behavioral asymmetries and mating success. Μales at all exposures (control, LC10, and LC30), that first approached their mate, showed right-biased tendency (approached their mate from their right side) in mate recognition. Females, however, showed variation in this behavior between the three exposures. Right-biased tendency of males in all treatment scenarios led to a higher percentage of successful copulations compared to the three other directions. For males that first approached their mate, the insecticide did not affect their lateralization of the first approach but did affect their copulation success. The duration of copulation time was reduced after the exposure to the insecticide, with the longest duration noted in the control females (63.0 s) and the lowest in the α-cypermethrin LC30 females (46.9 s). Moreover, at the α-cypermethrin LC10 exposure, mate recognition time was reduced, as opposed to α-cypermethrin LC30 exposure where mate recognition time was increased. These results can be further utilized to uncover the behavioral impacts of insecticides, enhancing the effectiveness of pest management in warehouses and poultry production facilities. Full article
(This article belongs to the Section Insect Pest and Vector Management)
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Graphical abstract
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<p>Flow chart of mating and courtship behavior of <span class="html-italic">Alphitobius diaperinus</span> male adults exposed to water-impregnated filter paper (control). Different lateralized traits exhibited by the males during each behavioral phase are indicated by the color of the arrows: orange for back-biased, red for front-biased, black for left-biased, and green for right-biased males. The width of each arrow indicates the percentage of insects engaging in each behavior (<span class="html-italic">n</span> = 70 pairs).</p>
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<p>Flow chart of mating behavior and courtship behavior of <span class="html-italic">Alphitobius diaperinus</span> female adults exposed to water-impregnated filter paper (control). Different lateralized traits exhibited by the females during each behavioral phase are indicated by the color of the arrows: orange for back-biased, red for front-biased, black for left-biased, and green for right-biased males. The width of each arrow indicates the percentage of insects engaging in each behavior (<span class="html-italic">n</span> = 40 pairs).</p>
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<p>Flow chart of mating and courtship behavior of <span class="html-italic">Alphitobius diaperinus</span> male adults exposed to α-cypermethrin LC<sub>10</sub>. Different lateralized traits exhibited by the males during each behavioral phase are indicated by the color of the arrows: orange for back-biased, red for front-biased, black for left-biased, and green for right-biased males. The width of each arrow indicates the percentage of insects engaging in each behavior (<span class="html-italic">n</span> = 98 pairs).</p>
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<p>Flow chart of mating and courtship behavior of <span class="html-italic">Alphitobius diaperinus</span> female adults exposed to α-cypermethrin LC<sub>10</sub>. Different lateralized traits exhibited by the females during each behavioral phase are indicated by the color of the arrows: orange for back-biased, red for front-biased, black for left-biased, and green for right-biased males. The width of each arrow indicates the percentage of insects engaging in each behavior (<span class="html-italic">n</span> = 32 pairs).</p>
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<p>Flow chart of mating and courtship behavior of <span class="html-italic">Alphitobius diaperinus</span> male adults exposed to α-cypermethrin LC<sub>30</sub>. Different lateralized traits exhibited by the males during each behavioral phase are indicated by the color of the arrows: orange for back-biased, red for front-biased, black for left-biased, and green for right-biased males. The width of each arrow indicates the percentage of insects engaging in each behavior (<span class="html-italic">n</span> = 93 pairs).</p>
Full article ">Figure 6
<p>Flow chart of mating and courtship behavior of <span class="html-italic">Alphitobius diaperinus</span> female adults exposed to α-cypermethrin LC<sub>30</sub>. Different lateralized traits exhibited by the females during each behavioral phase are indicated by the color of the arrows: orange for back-biased, red for front-biased, black for left-biased, and green for right-biased males. The width of each arrow indicates the percentage of insects engaging in each behavior (<span class="html-italic">n</span> = 60 pairs).</p>
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15 pages, 1649 KiB  
Article
Toxicity of Common Acaricides, Disinfectants, and Natural Compounds against Eggs of Rhipicephalus annulatus
by Samar M. Ibrahium, Abdel-Azeem S. Abdel-Baki, Sahar M. Gadelhaq, Shawky M. Aboelhadid, Hesham A. Mahran, Saleh Al-Quraishy, Abdulrahman Reyad and Asmaa A. Kamel
Pathogens 2024, 13(10), 824; https://doi.org/10.3390/pathogens13100824 - 24 Sep 2024
Viewed by 597
Abstract
Ticks pose a significant threat due to their ability to lay thousands of eggs, which can persist in the environment for extended periods. While the impact of various compounds on adult and larval ticks has been studied, research on their efficacy against tick [...] Read more.
Ticks pose a significant threat due to their ability to lay thousands of eggs, which can persist in the environment for extended periods. While the impact of various compounds on adult and larval ticks has been studied, research on their efficacy against tick eggs is limited. This study evaluated the ovicidal activity of commercial acaricides, disinfectants, and natural products against Rhipicephalus annulatus eggs using the egg hatch assay (EHA). Deltamethrin and cypermethrin caused a non-significant inhibition of hatching (IH%), even at concentrations higher than the recommended levels. By contrast, the acaricides chlorpyrifos, phoxim, and amitraz significantly inhibited hatching at all tested concentrations. Ivermectin also demonstrated significant IH% at various concentrations but did not fully inhibit the hatching process. Among the disinfectants tested, Virkon-S®, TH4, and Chlorox showed insignificant effects, whereas formalin achieved an IH% of only 34.1% at a high concentration of 200 mg/mL. Natural products, carvacrol and thymol, exhibited significant ovicidal activity, with a significant IH%. In a semi-field application, phoxim (0.5 mg/mL) and deltamethrin (0.05 mg/mL) were sprayed on tick eggs on pasture soil from a farm. The results indicated that phoxim-treated eggs had a 40% IH%, while deltamethrin-treated eggs showed only an 8.79% IH%. In conclusion, the acaricides amitraz, phoxim, and chlorpyrifos, as well as the natural products carvacrol and thymol, caused significant toxicity to R. annulatus eggs. Full article
(This article belongs to the Collection Advances in Tick Research)
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<p>Dose–probit hatchability curve of treated against eggs of <span class="html-italic">R. annulatus</span>; (<b>A</b>) deltamethrin-treated eggs, (<b>B</b>) cypermethrin-treated eggs, (<b>C</b>) cholorpyrifos-treated eggs, (<b>D</b>) phoxim-treated eggs, (<b>E</b>) amitraz-treated eggs, and (<b>F</b>) ivermectin-treated eggs.</p>
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<p>Percentage inhibition of hatching (IH%) of <span class="html-italic">R. annulatus</span> eggs treated by different concentrations of ivermectin.</p>
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<p>Percentage inhibition of hatching (IH%) of <span class="html-italic">R. annulatus</span> eggs treated by natural products of plant origin.</p>
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<p>Dose–probit hatchability curve of treated against eggs of <span class="html-italic">R. annulatus</span>; (<b>A</b>) carvacrol-treated eggs and (<b>B</b>) thymol-treated eggs.</p>
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12 pages, 2113 KiB  
Article
Development of a Selective Spectrophotometric Method for Deltamethrin Using Silver Nanoparticles
by Giovana A. Ferrari, Mayra A. Nascimento, Esteffany L. Bernardo, Marcela O. B. Cortêz, Alvaro V. N. C. Teixeira, André F. Oliveira and Renata P. L. Moreira
Processes 2024, 12(9), 2041; https://doi.org/10.3390/pr12092041 - 22 Sep 2024
Viewed by 489
Abstract
The present work proposes a spectrophotometric method for deltamethrin determination using silver nanoparticles (AgNPs). The AgNPs are spherical with a diameter of~11 nm and a negative surface charge with zeta potential ranging from −4.1 mV (pH 2) to −48 mV (pH 10). The [...] Read more.
The present work proposes a spectrophotometric method for deltamethrin determination using silver nanoparticles (AgNPs). The AgNPs are spherical with a diameter of~11 nm and a negative surface charge with zeta potential ranging from −4.1 mV (pH 2) to −48 mV (pH 10). The AgNP colloidal system showed greater stability at higher pH values and for a molar ratio of 6 between the sodium borohydride and silver nitrate in the synthesis. This is because the borate ions from the oxidation of borohydride are present on the surface of the nanoparticles, promoting an electrostatic repulsion between them which keeps them dispersed. The method was validated, obtaining satisfactory results of veracity and precision, and the limits of detection and quantification were 0.17 and 0.51 mg L−1, respectively. The method was selective for deltamethrin compared to the compounds cypermethrin, endosulfan, thiamethoxam, atrazine, chlorpyrifos and parathion. Deltamethrin promotes the formation of dendritic silver nanostructures, changing the color of the system. The results demonstrate the development of a reliable and selective method for the detection of deltamethrin using AgNPs. Full article
(This article belongs to the Section Chemical Processes and Systems)
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<p>Image of suspensions of silver nanoparticles obtained by TEM. (<b>A</b>) typical shape and size of a single AgNP; (<b>B</b>) agglomerated AgNPs.</p>
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<p>Kinetic study of AgNPs in contact with deltamethrin. (<b>A</b>) Molecular absorption spectrum monitored from 0–20 min. The different colors represent the band’s position over time; the insert in (<b>A</b>) shows the λ<sub>ABS/2</sub> monitoring; (<b>B</b>) monitoring of the SPR band at 400 nm (■) and monitoring of the of the half-height band of the isosbestic point—λ<sub>ABS/2</sub> (<span style="color:red">●</span>). Experimental conditions: [AgNPs]<sub>initial</sub> = 250 µmol L<sup>−1</sup>; [deltamethrin]<sub>initial</sub> = 2.50 mg L<sup>−1</sup>; room temperature = 23 ± 2 °C.</p>
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<p>(<b>A</b>) Temporal correlation curve obtained by DLS for AgNPs in the presence of deltamethrin as a function of time. The different colors represent the curve’s position over time. The continuous lines are fit using the sum of two exponentials decays. (<b>B</b>) Size distributions of AgNPs in the presence of deltamethrin as a function of time. Experimental conditions: [AgNPs]<sub>initial</sub>: 250 µmol L<sup>−1</sup>; [deltamethrin]<sub>initial</sub> = 250 mg L<sup>−1</sup>; room temperature = 23 ± 2 °C. The results for population d<sub>1</sub> are shown in black, and the arrow points to the axis that should be observed. The results for population d<sub>2</sub> are shown in red, and the arrow points to the axis that should be observed.</p>
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<p>Images obtained by TEM. (<b>A</b>,<b>B</b>) AgNPs in the presence of ACN, without deltamethrin; (<b>C</b>,<b>D</b>) AgNPs in the presence of deltamethrin.</p>
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<p>Method selectivity employing AgNPs: (<b>A</b>) water; (<b>B</b>) ACN; (<b>C</b>) cypermethrin; (<b>D</b>) deltamethrin; (<b>E</b>) atrazine; (<b>F</b>) endosulfan; (<b>G</b>) chlorpyrifos; (<b>H</b>) thiamethoxam; (<b>I</b>) parathion. Experimental conditions: ACN = 25% (<span class="html-italic">v</span>/<span class="html-italic">v</span>); pesticides concentration = 10 mg L<sup>−1</sup>.</p>
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11 pages, 2042 KiB  
Communication
Monitoring of Non-Maximum-Residue-Level Pesticides in Animal Feed: A Study from 2019 to 2023
by Roberta Giugliano, Vittoria Armenio, Valentina Savio, Erica Vaccaro, Valentina Ciccotelli and Barbara Vivaldi
Toxics 2024, 12(9), 680; https://doi.org/10.3390/toxics12090680 - 19 Sep 2024
Viewed by 588
Abstract
Pesticides play a critical role in modern agriculture by protecting crops and ensuring higher yields, but their widespread use raises concerns about human health and environmental impact. Regulatory agencies impose Maximum Residue Levels (MRLs) to ensure safety, and the European Food Safety Authority [...] Read more.
Pesticides play a critical role in modern agriculture by protecting crops and ensuring higher yields, but their widespread use raises concerns about human health and environmental impact. Regulatory agencies impose Maximum Residue Levels (MRLs) to ensure safety, and the European Food Safety Authority (EFSA) assesses pesticide risks. This study monitored pesticide residues in 169 feed samples from Piedmont (Italy) collected between 2019 and 2023. Using GC-MS/MS, residues were found in 92% of animal-based and 70% of cereal-based feedstuffs. The most common pesticides in cereal-based feeds were pyrimiphos-methyl, deltamethrin, cypermethrin, azoxystrobin, and tetramethrin, and the pesticide synergist piperonyl-butoxide demonstrated a significant increase in contaminated samples in 2023. The lower concentrations in 2021 were likely due to COVID-19 impacts on pesticide availability. In animal-based feeds, common pesticides included deltamethrin, cypermethrin, and the pesticide synergist piperonyl-butoxide. The results highlight the pervasive presence of low-dose pesticide mixtures in feed and food chains, which could impact health, although do not pose acute risks. The study emphasizes the need for ongoing pesticide monitoring and awareness of the long-term effects of chronic pesticide exposure on animal, human, and environmental health. Full article
(This article belongs to the Section Agrochemicals and Food Toxicology)
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<p>Number of cereal-based feedstuff samples contaminated by pesticides in 2021, 2022, and 2023. Asterisk refers to compounds not detected in any samples throughout the three years.</p>
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<p>Annual trends of concentrations of residues detected from 2021 to 2023 in cereal-based feed.</p>
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<p>Number of animal-origin-based feedstuff samples contaminated by pesticides from 2019 to 2023. Asterisk refers to compounds not detected in any samples throughout the three years.</p>
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<p>Annual trend of the concentration of the residues detected from 2019 to 2023 in animal origin-based feed.</p>
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15 pages, 975 KiB  
Article
Monitoring and Detection of Insecticide Resistance in Spodoptera frugiperda (Lepidoptera: Noctuidae): Evidence for Field-Evolved Resistance in Egypt
by Moataz A. M. Moustafa, Nourhan A. El-Said, Nawal AbdulAziz Alfuhaid, Fatma M. A. Abo-Elinin, Radwa M. B. Mohamed and Ahmed A. A. Aioub
Insects 2024, 15(9), 705; https://doi.org/10.3390/insects15090705 - 16 Sep 2024
Cited by 1 | Viewed by 783
Abstract
Spodoptera frugiperda (J.E. Smith) (Noctuidae: Lepidoptera) is a notable insect pest that invades major cereal crops, causing significant damage and loss. Resistances of 2nd instar larvae of two Egyptian field populations of S. frugiperda, collected from the Fayoum and Giza governments, were [...] Read more.
Spodoptera frugiperda (J.E. Smith) (Noctuidae: Lepidoptera) is a notable insect pest that invades major cereal crops, causing significant damage and loss. Resistances of 2nd instar larvae of two Egyptian field populations of S. frugiperda, collected from the Fayoum and Giza governments, were measured against eight insecticides, including traditional insecticides (profenofos and cypermethrin), bio-insecticides (emamectin benzoate, spinosad, and Bacillus thuringiensis), and insect growth regulators (IGRs) (lufenuron, diflubenzuron, and methoxyfenozide). In addition, the synergistic effects of three synergists (Piperonyl butoxide (PBO), diethyl maleate (DEM), and triphenyl phosphate (TPP) were assessed, and the activities of detoxification enzymes (acetylcholine esterase (AChE), cytochrome P-450 (CYP-450), carboxylesterase (CarE), and glutathione-s-transferase (GST) were also determined. Resistance surveillance revealed that the Fayoum field population showed moderate resistance to cypermethrin (RR = 5.75-fold), followed by spinosad (RR = 2.62-fold), and lufenuron (2.01-fold). On the other hand, the Giza population exhibited significant resistance to cypermethrin only (RR = 3.65-fold). Our results revealed that emamectin benzoate was the most effective insecticide, with an LC50 value of 0.003 mg/L for the Fayoum population and 0.001 mg/L for the Giza population, compared to the susceptible strain (0.005 mg/L). Among the biological insecticides, Bacillus thuringiensis was the least toxic insecticide of all the tested strains. Synergism assays indicated that DEM and TPP had the most synergistic effect on spinosad (SR = 8.00-fold for both), followed by PBO (SR = 5.71-fold) for the Fayoum population, compared with spinosad alone. The assay of detoxification enzymes showed that GST activity significantly (p < 0.05) increased in the two field strains compared to the susceptible strain. However, no significant changes were observed among the tested strains in CYP-450, CarE, or AChE. The findings of this study provide substantial insights into tracking and managing the development of insecticide resistance in S. frugiperda in Egypt. Full article
(This article belongs to the Special Issue Chemical Toxicology and Insecticide Resistance on Insect Pests)
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<p>Carboxylesterases (CarE; <b>a</b>), cytochrome p-450 (CYP-450; <b>b</b>), glutathione-s-transferase (GST; <b>c</b>) and acetylcholinesterase (AChE; <b>d</b>) activities in the 2nd instar larvae of a susceptible strain and two field populations of <span class="html-italic">S. frugiperda</span>. Each column represents the mean ± SEM of three independent experiments. <span class="html-italic">p</span>-values were determined using Tukey’s HSD test. Different letters above the bar indicate significant differences (<span class="html-italic">p</span> &lt; 0.05).</p>
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17 pages, 4413 KiB  
Article
Ameliorative Role of Vitamin C against Cypermethrin Induced Oxidative Stress and DNA Damage in Labeo rohita (Hamilton, 1822) Using Single Cell Gel Electrophoresis
by Sana Ullah, Amina Zuberi, Imdad Ullah and Mahmoud M. Azzam
Toxics 2024, 12(9), 664; https://doi.org/10.3390/toxics12090664 - 12 Sep 2024
Viewed by 717
Abstract
The present study was undertaken to evaluate cypermethrin (CYP)-induced oxidative stress [reactive oxygen species (ROS) and lipid peroxidation (LPO) in gills, muscles, brain, and liver tissues] and DNA damage/genotoxicity (peripheral blood erythrocytes) in a freshwater teleost rohu (Labeo rohita) and the [...] Read more.
The present study was undertaken to evaluate cypermethrin (CYP)-induced oxidative stress [reactive oxygen species (ROS) and lipid peroxidation (LPO) in gills, muscles, brain, and liver tissues] and DNA damage/genotoxicity (peripheral blood erythrocytes) in a freshwater teleost rohu (Labeo rohita) and the protective role of vitamin C. The LC50 of CYP against rohu was found to be 4.5 µg/L in a semi-static culture system through probit analysis. Fingerlings of rohu were distributed into four groups (Group 1st served as a control, fed 35% protein basal diet and was not exposed to CYP; Group 2nd was fed a basal diet and exposed to CYP; Group 3rd and Group 4th were fed diets supplemented with vitamin C at the rate of 100 and 200 mg/kg diet, respectively, and exposed to CYP). Fingerlings were reared on a basal and vitamin C-supplemented diet for 28 days prior to exposure to CYP. The results indicate a time-dependent significant increase in ROS and LPO (indicated by time course increase in TBARS level) as well as DNA damage in terms of number of comets, % DNA in tail, tail moment, tail length, and olive tail moment after exposure to LC50 of CYP. However, statistically comparable results in both Groups 1st and 4th indicate the protective role of vitamin C. The results reveal the effectiveness of vitamin C as a feed additive for countering pesticides toxicity in Labeo rohita. The current study indicates CYP as a potential genotoxicant for fish and classifies SCGE as a reliable and sensitive tool for assessing DNA damage. Full article
(This article belongs to the Special Issue Advances in Chemical Exposure and Environmental Risk)
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<p>Reactive oxygen species (ROS) in gills, muscles, brain, and liver tissues of rohu, <span class="html-italic">Labeo rohita</span> (nM DCF/g wet wt.; % of control). Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant difference at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Lipid peroxidation (LPO; μmol/min/mg protein) levels in gills, brain, muscles, and liver tissues of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant difference at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Number of comets per 120 cells observed in peripheral erythrocytes of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant difference at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Length (µm) of comets formed in peripheral blood erythrocytes of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant differences at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Tail length (µm), formed in peripheral erythrocytes of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant differences at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Head length (µm) of comets in peripheral erythrocytes of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant differences at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Percent DNA in tail (%) of comets in peripheral erythrocytes of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant differences at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Tail moment of comets in peripheral erythrocytes of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant difference at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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<p>Olive tail moment of comets in peripheral erythrocytes of rohu, <span class="html-italic">Labeo rohita</span>. Data (presented as mean ± S.E.; N = 9) were analyzed using ANOVA followed by HSK Tukey test. Different symbols on the bars show significant difference at <span class="html-italic">p</span> &lt; 0.05, whereas the same symbol indicates no significant difference.</p>
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16 pages, 577 KiB  
Article
Dynamics of Bactrocera dorsalis Resistance to Seven Insecticides in South China
by Xinlian Li, Peizheng Li, Doudou Li, Xinyan Cai, Shiwei Gu, Ling Zeng, Daifeng Cheng and Yongyue Lu
Insects 2024, 15(9), 679; https://doi.org/10.3390/insects15090679 - 8 Sep 2024
Viewed by 608
Abstract
Bactrocera dorsalis is a highly invasive and destructive pest distributed worldwide. Chemical insecticides remain the primary measure for their control; however, this species has already developed resistance to several insecticides. In recent years, there have been several reports of monitoring B. dorsalis resistance [...] Read more.
Bactrocera dorsalis is a highly invasive and destructive pest distributed worldwide. Chemical insecticides remain the primary measure for their control; however, this species has already developed resistance to several insecticides. In recent years, there have been several reports of monitoring B. dorsalis resistance in China, but continuous monitoring results are lacking and do not even span a decade. In this study, we monitored the dynamics of resistance to seven insecticides among 11 geographically distinct Chinese populations of B. dorsalis (2010–2013; follow-up in 2023). The 11 populations were found to adapt rapidly to antibiotic insecticides (spinosad, emamectin benzoate, and avermectin), reaching high levels of insecticide resistance in several areas. Overall, a decreasing trend in resistance to organophosphorus insecticides (chlorpyrifos and trichlorfon) was observed, whereas pyrethroid (beta-cypermethrin and cyhalothrin) resistance trends were observed to both increase and decrease. The monitoring of field resistance among different B. dorsalis populations over the duration of this study is important for improving the efficiency and sustainability of agricultural pest management, and the results provide a scientific basis for the development of more effective resistance management strategies. Full article
(This article belongs to the Special Issue Monitoring and Management of Invasive Insect Pests)
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<p><span class="html-italic">Bactrocera dorsalis</span> collection sites.</p>
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12 pages, 3504 KiB  
Article
Transgenerational Sub-Lethal Pyrethroid Exposure Affects Shape Variation and Fluctuating Asymmetry in Seed Beetles
by Sanja Budečević, Dragana Predojević, Mirko Đorđević, Lea Vlajnić, Oliver Stojković, Biljana Stojković and Uroš Savković
Symmetry 2024, 16(8), 995; https://doi.org/10.3390/sym16080995 - 6 Aug 2024
Viewed by 655
Abstract
One method of crop protection is the application of a widely used group of pesticides—pyrethroids. As xenobiotics, sub-lethal doses of insecticides cause stress in pests, resulting in a change in the shape and size of their organs or bodies. The stress caused by [...] Read more.
One method of crop protection is the application of a widely used group of pesticides—pyrethroids. As xenobiotics, sub-lethal doses of insecticides cause stress in pests, resulting in a change in the shape and size of their organs or bodies. The stress caused by pesticides may lead to acute destabilization of development, but also to transgenerational canalization through the process of genetic assimilation. Fluctuating asymmetry (FA), small random deviations between the right and left sides of bilaterally symmetrical traits, is an outcome of developmental instability and is a measurable indicator of phenotypic response to stress. We exposed four populations of the seed beetle Acanthoscelides obtectus to sub-lethal doses of cypermethrin for ten generations in a laboratory evolution experiment. Using geometric morphometrics, we analyzed size and shape changes and the level of fluctuating asymmetry in untreated beetles and in samples from the fifth and tenth generation. Exposure over ten generations led to an increase in the body size of the beetles, shortening of their pronotum and elongation of their thorax and abdomen. After ten generations of exposure to cypermethrin, FA levels decreased, indicating a canalization of development. This study provides new insights into the phenotypic markers of environmental pollution from agricultural activities. Full article
(This article belongs to the Section Life Sciences)
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<p>Experimental design using an experimental evolution approach in which beetles were exposed to a sub-lethal dose of cypermethrin (LD<sub>20</sub>) for ten generations. Beetles were sampled from the base population and after five and ten generations of cypermethrin exposure.</p>
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<p>Morphospaces of seed beetles before (<b>a</b>) and after (<b>b</b>) size correction along the first two PC axes. The presented shape changes correspond to the minimum and maximum PC scores in the scatterplots and are shown as wireframe diagrams.</p>
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<p>Effects of sub-lethal doses of cypermethrin after five and ten generations of exposure on the shape of beetles before (<b>a</b>) and after (<b>b</b>) correction for size, shown in a scatterplot with canonical variables.</p>
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<p>Shape changes (<b>a</b>) between G0 and G5 experimental groups and (<b>b</b>) between G0 and G10 experimental groups, shown as wireframe diagrams before and after size correction. G0 is presented as a black diagram, while G5 and G10 are presented as a gray diagram.</p>
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<p>Fluctuating asymmetrical variations in shape for the G0, G5 and G10 experimental groups of <span class="html-italic">A. obtectus</span>. Statistically significant differences between the FA10a indexes are marked as *** for <span class="html-italic">p</span> &lt; 0.0001 and ** for <span class="html-italic">p</span> ≤ 0.01.</p>
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11 pages, 1263 KiB  
Article
Evaluation of an Attract-and-Kill Strategy Using Long-Lasting Insecticide Nets for the Management of the Brown Marmorated Stink Bug in Northern Italy
by Antonio Masetti, Agata Morelli, Luca Fagioli, Gianfranco Pradolesi, Riccardo Nicoli, Olmo Scagliarini, Maria Grazia Tommasini and Michele Preti
Insects 2024, 15(8), 577; https://doi.org/10.3390/insects15080577 - 29 Jul 2024
Cited by 2 | Viewed by 812
Abstract
The brown marmorated stink bug (BMSB), Halyomorpha halys (Stål) (Hemiptera: Pentatomidae), is causing extensive economic losses in tree fruit crops. Including attract-and-kill (AK) strategies targeting BMSBs in an integrated pest management framework could reduce the amounts of insecticides sprayed and benefit growers, consumers [...] Read more.
The brown marmorated stink bug (BMSB), Halyomorpha halys (Stål) (Hemiptera: Pentatomidae), is causing extensive economic losses in tree fruit crops. Including attract-and-kill (AK) strategies targeting BMSBs in an integrated pest management framework could reduce the amounts of insecticides sprayed and benefit growers, consumers and the environment. This study evaluated the effectiveness of an area-wide AK strategy across an intensive fruticulture region of Northern Italy, comparing four paired pear sites with and without two AK stations ha−1. These stations consisted of long-lasting insecticide-treated nets containing alpha-cypermethrin, baited with the BMSB aggregation pheromone and synergist. BMSB abundance was estimated using black-standing monitoring traps, and fruit damage upon harvest was recorded across all sites. The AK stations did not decrease the BMSB abundance nor the fruit damage, while after harvest significantly lower BMSB captures were detected in the AK sites compared to the control sites. Whilst the lures’ efficacy was corroborated by this research, the killing method requires improvement and refinement. Full article
(This article belongs to the Section Insect Pest and Vector Management)
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<p>Locations of the sampling sites in Emilia-Romagna (Northern Italy), where orange and blue circles represent the control and AK strategies, respectively, and the arrangement of the AK and monitoring stations in relation to the experimental sites. The partitioning within the Emilia-Romagna region represents the provinces. Exact geographic positions can be found in <a href="#app1-insects-15-00577" class="html-app">Table S3</a>.</p>
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<p><span class="html-italic">Halyomorpha halys</span> individuals caught by black-standing monitoring traps deployed either in AK sites (blue line) or in controls (yellow line) in the early part of the season (April–July 2021). The GLMM did not detect any significant effects on the captures due to the presence of AK stations.</p>
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<p><span class="html-italic">Halyomorpha halys</span> individuals caught by black-standing monitoring traps deployed either in AK sites (blue line) or in controls (yellow line) in the late part of the season (August–October 2021). A significant reduction in captures was detected by the GLMM in the sites where AK stations were set up compared to the control sites.</p>
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18 pages, 3269 KiB  
Article
Comparative Population Biology and Related Gene Expression in the Beta-Cypermethrin-Resistant Strains of Bactrocera dorsalis (Hendel)
by Doudou Li, Langjie Chen, Xinyan Cai, Yixiang Qi and Yongyue Lu
Insects 2024, 15(8), 569; https://doi.org/10.3390/insects15080569 - 26 Jul 2024
Viewed by 657
Abstract
Diptera and Lepidoptera species have the highest levels of insecticide resistance, and the mechanism of drug resistance has been studied in detoxification metabolism genes such as P450, GST, EST, and ABC. Since Bactrocera dorsalis are resistant to a variety of chemicals, the pattern [...] Read more.
Diptera and Lepidoptera species have the highest levels of insecticide resistance, and the mechanism of drug resistance has been studied in detoxification metabolism genes such as P450, GST, EST, and ABC. Since Bactrocera dorsalis are resistant to a variety of chemicals, the pattern and mechanism of resistance in Bactrocera dorsalis have been investigated from a variety of aspects such as detoxification metabolism genes, detoxification enzymes, intestinal symbiotic bacteria, and synergists in the world. In this study, 51 species and 149 detoxification metabolism genes were annotated in the Suppression Subtractive Hybridization (SSH) library, and 12 candidate genes related to beta-cypermethrin resistance were screened and quantitatively expressed in this library. Two genes were found to be upregulated in the egg stage, three genes in the larval stage, one gene in the pupal stage, and five genes in the adult stage, and four genes were found to be upregulated in the midgut and the malacca ducts in the midgut. The expression of cyp6g1, cyp6a22, GST-Epsilon9, and Trypsin-4 genes was upregulated in resistant strains, with the most obvious upregulation occurring in the midgut and the Malpighian tubules. These results provide new insights into the study of pesticide resistance in quarantine insects. Full article
(This article belongs to the Section Insect Physiology, Reproduction and Development)
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<p>Dynamics of daily fecundity in females of beta-cypermethrin-resistant and -sensitive strains.</p>
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<p>Dynamics of adult survival rates of beta-cypermethrin-resistant and -sensitive strains of the oriental fruit fly.</p>
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<p>Distribution of SSH library data of the beta-cypermethrin-resistant strains of the oriental fruit fly.</p>
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<p>Distribution of species in SSH library sequences. (<b>a</b>) Distribution of species with homology in SSH library sequences; (<b>b</b>) distribution of species with high homology in SSH library sequences.</p>
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<p>Sequence annotation plot of the SSH library for the resistant beta-cypermethrin strains. (<b>a</b>) Classification map of biological pathways (Level 2); (<b>b</b>) classification diagram of cellular components (Level 2); (<b>c</b>) classification map of molecular functions (Level 2).</p>
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<p>Relative expression of the target genes of the three strains of the oriental fruit fly at different developmental states. Note: Quotation marks placed to the upper right of letters indicate grouping, and different letters in the same row within a group indicate significant differences at the 0.05 level (Duncan’s method).</p>
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<p>Relative expression of target genes in different tissues of three strains of adult oriental fruit fly. Note: Ot: other tissues; Gt: midgut; Mt: Malpighian tubules; Fb: fat body; Rg: reproductive gland.</p>
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18 pages, 2711 KiB  
Article
Volatile Organic Compound Emission Inventory for Pesticide Spraying in an Agricultural City of Northeast China: Real-Time Monitoring and Method Optimization
by Ruimin Li, Zixuan Xia, Bo You, Bowen Shi and Jing Fu
Agriculture 2024, 14(8), 1223; https://doi.org/10.3390/agriculture14081223 - 25 Jul 2024
Viewed by 730
Abstract
Atmospheric volatile organic compounds (VOCs), such as olefins and aromatics, released from synthetic chemical pesticide sprays can increase regional air pollution, public health risks, and food security risks. However, significant uncertainties remain regarding the measurement methods and chemical profiles of VOC emissions. Using [...] Read more.
Atmospheric volatile organic compounds (VOCs), such as olefins and aromatics, released from synthetic chemical pesticide sprays can increase regional air pollution, public health risks, and food security risks. However, significant uncertainties remain regarding the measurement methods and chemical profiles of VOC emissions. Using an agricultural city, Changchun City in Northeast China, as a case study, we quantified real-time concentration and composition data based on online monitoring instruments for the year 2023. This study optimized data collection methods for emission factors and activity levels and developed a high-precision emission inventory of VOCs in pesticides at the city scale. The emission factors for VOCs from the seven categories of pesticides were estimated as follows: 78 g/kg (nicosulfuron and atrazine, oil-dispersible [OD] and suspension emulsion [SE], respectively), 4 g/kg (chlorpyrifos and indoxair conditioningarb, suspension concentrate [SC]), 5 g/kg (fluopicolide and propamocarb hydrochloride, SC), 217 g/kg (MCPA-dimethylammonium, aqueous solution [AS]), 34 g/kg (glyphosate, AS), 575 g/kg (beta-cypermethrin and malathion, emulsifiable concentrate [EC]), and 122 g/kg (copper abietate, emulsion in water [EW]), depending on the pesticide formulation components and formulation types. The orchard insecticide exhibited the highest emission factors among all pesticides owing to its emulsifiable concentrate formulation and 80% content of inactive ingredients (both factors contribute to the high content of organic solvents in the pesticide). The major components of VOC emissions from pesticide spraying were halocarbons (27–44%), oxygenated VOCs (OVOCs) (25–38%), and aromatic hydrocarbons (15–28%). The total VOC emissions from pesticide spraying in the Changchun region accounted for 10.6 t, with Yushu City contributing 28% of the VOC emissions and Gongzhuling City and Dehui City contributing 18.7% and 16.0%, respectively. Herbicides were the main contributors to VOC emissions because of their high emission factors and extensive use in fields (used for spraying maize and rice, the main crops in Changchun City). May and June exhibited the highest VOC emissions from pesticide application, with May accounting for 57.0% of annual pesticide emissions, predominantly from herbicides (95.1%), followed by insecticides (4.9%). June accounted for 30.1% of the annual pesticide emissions, with herbicides being the largest contributor of VOC emissions. An emission inventory of VOC with a monthly scale and spatial grid resolutions of 0.083° and 0.5° in 2023 was developed. These emission factors and inventories of pesticide applications provide valuable information for air quality modeling. This study also provides an important scientific basis for enhancing regional air quality and mitigating the environmental impact of pesticide use in major grain-producing areas. Full article
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<p>Study region (<b>a</b>) and experimental equipment (<b>b</b>) (The red star indicates the locations of experimental monitoring stations).</p>
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<p>(<b>a</b>). Time series of meteorological parameters and levels of air pollutants during pesticide spraying (e.g., paddy herbicides, dryland herbicides, orchard insecticides, and orchard fungicides). (<b>b</b>). Time series of meteorological parameters and levels of air pollutants during pesticide spraying (orchard herbicides, dryland and paddy fungicides, and dryland and paddy insecticides).</p>
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<p>The relative contributions of the individual VOC species from pesticide spraying. Types of pesticides are as follows: (<b>a</b>) Nicosulfuron and atrazine (<b>b</b>) Indoxair conditioningarb and chlorpyrifos (<b>c</b>) Fluopicolide and propamocarb hydrochloride (<b>d</b>) MCPA-dimethylammonium (<b>e</b>) Beta-cypermethrin and malathion (<b>f</b>) Copper bietate (<b>g</b>) Glyphosate. (<b>1.</b> Acetone. <b>2.</b> 4-Bromofluorobenzene. <b>3.</b> Chloromethane. <b>4.</b> Methylene chloride. <b>5.</b> 2-Butanone. <b>6.</b> Propene. <b>7.</b> Benzene. <b>8.</b> Naphthalene. <b>9.</b> Ethyl acetate. <b>10.</b> 1,2-Dichloroethane. <b>11.</b> Toluene. <b>12.</b> 1,2,4-Trichlorobenzene. <b>13.</b> Acrolein. <b>14.</b> Dichlorodifluoromethane. <b>15.</b> m-Xylene. <b>16.</b> Hexane. <b>17.</b> 2-Hexanone. <b>18.</b> Hexachloro-1,3-butadiene. <b>19.</b> 2-Propanol. <b>20.</b> 1,2-Dichloropropane. <b>21.</b> 1,2-Dichlorobenzene. <b>22.</b> Carbon disulfide. <b>23.</b> 1,4-Dichlorobenzene. <b>24.</b> 1,2,4-trimethylbenzene. <b>25.</b> 1,3-dichlorobenzene. <b>26.</b> Chloroform. <b>27.</b> o-Xylene. <b>28.</b> 4-Methyl-2-pentanone. <b>29.</b> 1,1,2-trichloro-1,2,2-trifluoroethane. <b>30.</b> Carbon tetrachloride. <b>31.</b> Cyclohexane. <b>32.</b> Methyl tert-butyl ether. <b>33.</b> Styrene. <b>34.</b> Ethyl benzene. <b>35.</b> 1,3,5-Trimethylbenzene. <b>36.</b> Tetrahydrofuran. <b>37.</b> Methyl methacrylate. <b>38.</b> Benzyl chloride. <b>39.</b> 4-Ethyltoluene. <b>40.</b> Vinyl chloride. <b>41.</b> Heptane. <b>42.</b> Tetrachloroethylene. <b>43.</b> Bromomethane. <b>44.</b> 1,1,2-Trichloroethane. <b>45.</b> Dibromochloromethane. <b>46.</b> Ethylene dibromide. <b>47.</b> 1,1,2,2-tetrachloroethane. <b>48.</b> Chlorobenzene. <b>49.</b> Trans 1,3-dichloropropene. <b>50.</b> Bromoform. <b>51.</b> Trichloroethylene. <b>52.</b> 1,1-Dichloroethane. <b>53.</b> 1,4-Dioxane. <b>54.</b> cis-1,3-Dichloropropene. <b>55.</b> 1,1-Dichlorethene. <b>56.</b> Vinyl acetate. <b>57.</b> 1,3-butadiene. <b>58.</b> Bromodichloromethane. <b>59.</b> 1,1,2,2-Tetrachloro-ethylene dichloride. <b>60.</b> trans-1,2-Dichloroethene. <b>61.</b> 1,1,1-trichloroethane. <b>62.</b> cis-1,2-dichloroethene. <b>63.</b> Dimethyl disulfide. <b>64.</b> Chlorethane. <b>65.</b> Trichlorofluoromethane.)</p>
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<p>(<b>a</b>). The spatial distribution of VOC emissions from pesticide spraying in the Changchun region (for three types of crops and three types of pesticides). (<b>b</b>). The spatial distribution of the total VOC emissions from pesticide spraying.</p>
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<p>The monthly VOC emissions and contribution rates from pesticide spraying in the Changchun region.</p>
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<p>(<b>a</b>). The spatial distribution of VOC emissions from pesticide spraying at county-level. (<b>b</b>). The spatial distribution of irrigated area in Changchun. (<b>c</b>). The spatial distribution of VOC emissions from pesticide spraying at 1 km<sup>2</sup> resolution.</p>
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<p>Sensitivity analysis of VOC emission reduction rates with emission factors, amount of pesticide applied per hectare, and pesticide application frequency.</p>
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22 pages, 24990 KiB  
Article
Functional Validation of Endogenous Redox Partner Cytochrome P450 Reductase Reveals the Key P450s CYP6P9a/-b as Broad Substrate Metabolizers Conferring Cross-Resistance to Different Insecticide Classes in Anopheles funestus
by Sulaiman S. Ibrahim, Mersimine F. M. Kouamo, Abdullahi Muhammad, Helen Irving, Jacob M. Riveron, Magellan Tchouakui and Charles S. Wondji
Int. J. Mol. Sci. 2024, 25(15), 8092; https://doi.org/10.3390/ijms25158092 - 25 Jul 2024
Viewed by 809
Abstract
The versatility of cytochrome P450 reductase (CPR) in transferring electrons to P450s from other closely related species has been extensively exploited, e.g., by using An. gambiae CPR (AgCPR), as a homologous surrogate, to validate the role of An. funestus [...] Read more.
The versatility of cytochrome P450 reductase (CPR) in transferring electrons to P450s from other closely related species has been extensively exploited, e.g., by using An. gambiae CPR (AgCPR), as a homologous surrogate, to validate the role of An. funestus P450s in insecticide resistance. However, genomic variation between the AgCPR and An. funestus CPR (AfCPR) suggests that the full metabolism spectrum of An. funestus P450s might be missed when using AgCPR. To test this hypothesis, we expressed AgCPR and AfCPR side-by-side with CYP6P9a and CYP6P9b and functionally validated their role in the detoxification of insecticides from five different classes. Major variations were observed within the FAD- and NADP-binding domains of AgCPR and AfCPR, e.g., the coordinates of the second FAD stacking residue AfCPR-Y456 differ from that of AgCPR-His456. While no significant differences were observed in the cytochrome c reductase activities, when co-expressed with their endogenous AfCPR, the P450s significantly metabolized higher amounts of permethrin and deltamethrin, with CYP6P9b-AfCPR membrane metabolizing α-cypermethrin as well. Only the CYP6P9a-AfCPR membrane significantly metabolized DDT (producing dicofol), bendiocarb, clothianidin, and chlorfenapyr (bioactivation into tralopyril). This demonstrates the broad substrate specificity of An. funestus CYP6P9a/-b, capturing their role in conferring cross-resistance towards unrelated insecticide classes, which can complicate resistance management. Full article
(This article belongs to the Section Biochemistry)
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<p><b>Comparison of Anopheles <span class="html-italic">CPR</span> amino acid sequences.</b> Af, Ag, Am, and Ast refer to <span class="html-italic">An. funestus</span>, <span class="html-italic">An. gambiae</span>, <span class="html-italic">An. minimus</span>, and <span class="html-italic">An. stephensi</span>, respectively. Predicted membrane-spanning domains are in solid green boxes; the cofactor-binding regions are in solid blue boxes; and critically important residues are in red, dashed boxes. Variable amino acids are in red.</p>
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<p><b>Three-dimensional folding of AfCPR and AgCPR models.</b> (<b>a</b>). Overlay of AfCPR and AgCPR models. Conserved critical residues and cofactors are in stick format and labelled. Residues are in warm pink and blue in AfCPR, and in orange and yellow in AgCPR. The DDAN-P450/<span class="html-italic">cytochrome c</span> binding sequence residues are highlighted in blue in AfCPR and yellow in AgCPR models. (<b>b</b>). Close shot of the FMN stacking residues showing a contrasting coordinate in Y<sup>178</sup> between AfCPR and AgCPR models. (<b>c</b>). Close shot of the FAD stacking residues showing the contrasting coordinates of Y<sup>456</sup> in AfCPR and H<sup>456</sup> in AgCPR models.</p>
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<p><b>ClusPro docking scores and PDBsum prediction of residues involved in CPR−P450 interactions.</b> Note: The crystal templates of 1TQN for CYP6P9a and 1AMO for CPR lack residues 1–22 and 1–66, respectively. Amino acid counts are thus +22 for Chain A (CYP6P9a) and +66 for Chain C (AfCPR/AgCPR). Blue lines are hydrogen bonds, and red lines are salt bridges.</p>
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<p><b>Comparative reductase activity of recombinant CPR proteins.</b> (<b>a</b>). Initial assessment of <span class="html-italic">cytochrome c</span> reductase activity. (<b>b</b>). Michaelis–Menten plot of <span class="html-italic">cytochrome c</span> reduction by recombinant AfCPR and AgCPR co-expressed side-by-side with CYP6P9a and CYP6P9b.</p>
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<p><b>Comparative profiling of impact of AfCPR on metabolism of insecticides</b>. (<b>a</b>). Substrate−depletion by the recombinantly co-expressed CYP6P9a and -b with either AfCPR or AgCPR. *, ** and *** = significantly different at <span class="html-italic">p</span> &lt; 0.05, <span class="html-italic">p</span> &lt; 0.01 and <span class="html-italic">p</span> &lt; 0.001, respectively. (<b>b</b>). HPLC chromatogram showing chlorfenapyr metabolism by CYP6P9a-AfCPR membrane, with tralopyril eluting before the 14th minute. (<b>c</b>). HPLC chromatogram showing DDT metabolism by CYP6P9a-AfCPR membrane, with dicofol eluting before the 8th minute. (<b>d</b>). Michaelis–Menten plot showing turnover of DDT metabolism by CYP6P9a-AfCPR membrane.</p>
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<p>Preparation of recombinant AfCPR with <span class="html-italic">pelB</span> leader and <span class="html-italic">tac-tac</span> promoter for expression in pACYC-184.</p>
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19 pages, 339 KiB  
Article
Exposure of Young Children to Permethrin and Cypermethrin Insecticides in the Residential Environment
by Siriporn Sirikanyaporn, Noppanun Nankongnab, Pornpimol Kongtip, Sukhontha Siri, William Alfred Suk and Susan Renee Woskie
Toxics 2024, 12(7), 477; https://doi.org/10.3390/toxics12070477 - 30 Jun 2024
Viewed by 856
Abstract
The aims of this study were to evaluate the exposure to permethrin and cypermethrin of young children aged between 2 and 5 years in Nakhon Pathom and Sing Buri provinces, Thailand. A questionnaire that included general demographic information, household characteristics, insecticide usage and [...] Read more.
The aims of this study were to evaluate the exposure to permethrin and cypermethrin of young children aged between 2 and 5 years in Nakhon Pathom and Sing Buri provinces, Thailand. A questionnaire that included general demographic information, household characteristics, insecticide usage and exposure-related behavior in children was used to interview parents or family caregivers. Permethrin and cypermethrin concentrations on floor surfaces and children’s hands, as well as their urinary metabolites, were analyzed by gas chromatography coupled with mass spectrometry. The results showed that permethrin and cypermethrin were detected in 62% and 83% of the children’s hand wipe samples, with geometric mean (GM) levels of 0.02 µg and 0.04 µg, respectively. Permethrin and cypermethrin were detected in 79% and 93% of floor surface wipe samples, with GM levels of 0.90 µg/m2, and 1.49 µg/m2, respectively. For children’s urine, the GM concentrations of cis- and trans-DCCA, 3-PBA, and total pyrethroid metabolites were 0.84, 0.31 and 1.23 nmol/g creatinine, respectively. This study found that household insecticide product usage and having a tile floor were associated with increased permethrin concentrations on the children’s hands and floor surfaces. However, cypermethrin concentrations on floor surfaces were significantly higher in families using aerosol insecticide sprays and insecticide products in the living room and bedroom. The predictors of the total pyrethroid, DCCA and 3-PBA metabolites are permethrin on children’s hands or floor surfaces and cypermethrin on floor surfaces. Full article
(This article belongs to the Section Human Toxicology and Epidemiology)
23 pages, 10381 KiB  
Article
Ovicidal Toxicity and Morphological Changes in Housefly Eggs Induced by the Essential Oils of Star Anise and Lemongrass and Their Main Constituents
by Hataichanok Passara, Sirawut Sittichok, Jirisuda Sinthusiri, Tanapoom Moungthipmalai, Cheepchanok Puwanard, Kouhei Murata and Mayura Soonwera
Insects 2024, 15(7), 481; https://doi.org/10.3390/insects15070481 - 27 Jun 2024
Cited by 1 | Viewed by 661
Abstract
This study attempted to evaluate the ovicidal activity of single-component formulations and combination formulations of lemongrass and star anise essential oils (EOs) and their main constituents against housefly eggs. The efficacies of the combinations were compared with those of single-component formulations and α-cypermethrin. [...] Read more.
This study attempted to evaluate the ovicidal activity of single-component formulations and combination formulations of lemongrass and star anise essential oils (EOs) and their main constituents against housefly eggs. The efficacies of the combinations were compared with those of single-component formulations and α-cypermethrin. Safety bioassays of all treatments and α-cypermethrin on non-target predators—guppy and molly—were conducted. Two combinations: 1% lemongrass EO + 1% trans-anethole and 1% star anise EO + 1% geranial, exhibited a strong ovicidal activity with an inhibition rate of 94.4 to 96.2%. They were 1.1 times as effective as α-cypermethrin. The two combinations also showed high synergistic activity compared to single-component formulations, with a high synergistic index and a high increased inhibition value of 37.4 to 57.7%. All EO treatments were benign for all non-target aquatic species with a high 50% lethal time (LT50) and safety index. In contrast, α-cypermethrin was highly toxic to them with a low LT50. The morphological abnormalities observed in housefly eggs at death were those such as the shrivelling of the eggs, aberrations and damage to the eggshells, hatching lines, aeropyles, plastron, and micropyle. The potential of these two combinations as a cypermethrin replacement is compelling. Full article
(This article belongs to the Special Issue Insect Vectors of Human and Zoonotic Diseases)
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<p>Light micrographs of housefly eggs: (<b>A</b>) dorsal view of a fertile egg aged 2–3 h showing the anterior pole (ap) on the left, the posterior pole (pp) on the right, the plastron (pt) on the median and the hatching line (hl) (green arrow); (<b>B</b>) a fertile egg aged 6 h; (<b>C</b>) a fertile egg aged 12 h; (<b>D</b>,<b>E</b>) the first instar larvae with posterior spiracles (ps) (green arrow); and (<b>F</b>) eggshell (es).</p>
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<p>Inhibition rate (%) ± SE versus exposure time of treatments, 1% α-cypermethrin, and drinking water against housefly eggs. Note: The mean inhibition rates within a column followed by a different letter differ significantly according to the Tukey’s test at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>The 50% lethal time (LT<sub>50</sub>) and 90% lethal time (LT<sub>90</sub>) of treatments and 1% α-cypermethrin against housefly eggs, and inhibition index (II) comparing the strength of treatments versus 1% α-cypermethrin. Note: II &gt; 1 suggests that the treatment was more toxic to housefly eggs than α-cypermethrin; II &lt; 1 suggests that the treatment was less toxic to housefly eggs than α-cypermethrin; and II = 1 suggests that the treatment was equally effective to α-cypermethrin.</p>
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<p>Increased inhibition value (IIV) and synergistic index (SYI) of two combinations compared to the corresponding single-component formulations. Note: SYI &gt; 1 signifies that there is a synergistic effect; SYI &lt; 1 signifies that there is an antagonistic effect; and SYI = 1 signifies that there is no synergistic nor antagonistic effect.</p>
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<p>Mortality rate (%) ± SE and LT<sub>50</sub> of single-component and combination formulations and 1% α-cypermethrin against non-target species: guppy (<b>A</b>) and molly (<b>B</b>). Note: Mean mortality rates within a column (1, 5, and 10 days) followed by a different letter differ significantly by Tukey’s test at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Safety index (SI) and safety ratio (SR) values of all treatments and 1% α-cypermethrin against non-target species: guppy (<b>A</b>) and molly (<b>B</b>). Note: An SI value greater than one was considered safe, while an SI value less than one was considered unsafe. SR &gt; 1 means that the treatment was safer for non-target aquatic species than 1% α-cypermethrin; SR &lt; 1 means that the treatment was more toxic to the non-target aquatic species than 1% α-cypermethrin; and SR = 1 means that the treatment was neither safer nor more toxic than 1% α-cypermethrin.</p>
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<p>(<b>A1</b>,<b>A2</b>) Light micrographs of housefly eggs showing a complete fertile egg; (<b>A3</b>) the first instar larva (l) and morphological changes induced by treatment, showing a damaged embryo and dead embryo inside the egg after being treated with 1% lemongrass EO (<b>B1</b>–<b>B3</b>), 1% star anise EO (<b>C1</b>–<b>C3</b>), 1% geranial (<b>D1</b>–<b>D3</b>), 1% <span class="html-italic">trans</span>-anethole (<b>E1</b>–<b>E3</b>), 1% lemongrass EO + 1% <span class="html-italic">trans</span>-anethole (<b>F1</b>–<b>F3</b>), and 1% star anise EO + 1% geranial (<b>G1</b>–<b>G3</b>). Note: Anterior pole (ap), posterior pole (pp), plastrons (pt), and eggshell (es).</p>
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<p>Scanning electron micrographs of the dorsal view of a housefly egg showing the normal egg surface with anterior pole (ap) on the left, posterior pole (pp) on the right, plastrons (pt), hatching line (hl) (white arrow) on the median of the untreated egg (<b>A</b>), and morphological changes induced by treatment, showing damages and abnormality of egg surfaces after the egg was treated with 1% lemongrass EO (<b>B</b>), 1% geranial (<b>C</b>), 1% star anise EO (<b>D</b>), 1% <span class="html-italic">trans</span>-anethole (<b>E</b>), 1% lemongrass EO + 1% <span class="html-italic">trans</span>-anethole (<b>F</b>), and 1% star anise EO + 1% geranial (<b>G</b>).</p>
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<p>Scanning electron micrographs of the median area of a housefly egg showing the normal hatching line (hl) (white arrow) and plastron (pt) of an untreated egg (<b>A</b>). They also show an abnormal and swollen hatching line and a damaged plastron after the egg was treated with 1% lemongrass EO (<b>B</b>), 1% geranial (<b>C</b>), 1% star anise EO (<b>D</b>), 1% <span class="html-italic">trans</span>-anethole (<b>E</b>), 1% lemongrass EO + 1% <span class="html-italic">trans</span>-anethole (<b>F</b>), and 1% star anise EO + 1% geranial (<b>G</b>).</p>
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<p>Scanning electron micrographs of the plastron of an untreated egg in closer view, showing normal islands with normal anastomosis (at) and aeropyles (ap) (white arrow) (<b>A</b>); damaged and swollen anastomosis and closed aeropyles after the egg was treated with 1% lemongrass EO (<b>B</b>), 1% geranial (<b>C</b>), 1% star anise EO (<b>D</b>), 1% <span class="html-italic">trans</span>-anethole (<b>E</b>), 1% lemongrass EO + 1% <span class="html-italic">trans</span>-anethole (<b>F</b>), and 1% star anise EO + 1% geranial (<b>G</b>).</p>
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<p>Scanning electron micrographs of a micropyle (mc) (white arrow) in the anterior region with smooth ornamentation and a single orifice in the middle of an untreated egg (<b>A</b>); an abnormal micropyle with rough ornamentation with swollen and closed orifice after the egg was treated with 1% lemongrass EO (<b>B</b>); 1% geranial (<b>C</b>); 1% star anise EO (<b>D</b>); 1% <span class="html-italic">trans</span>-anethole (<b>E</b>); 1% lemongrass EO + 1% <span class="html-italic">trans</span>-anethole (<b>F</b>); and 1% star anise EO + 1% geranial (<b>G</b>).</p>
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16 pages, 2890 KiB  
Article
Bioaccumulation of Organic and Inorganic Pollutants in Fish from Thermaikos Gulf: Preliminary Human Health Risk Assessment Assisted by a Computational Approach
by Konstantinos M. Kasiotis, Effrosyni Zafeiraki, Electra Manea-Karga, Demetrios Kouretas, Fotis Tekos, Zoi Skaperda, Nikolaos Doumpas and Kyriaki Machera
J. Xenobiot. 2024, 14(2), 701-716; https://doi.org/10.3390/jox14020041 - 1 Jun 2024
Cited by 1 | Viewed by 1477
Abstract
The monitoring of contaminants in fish species is pivotal for fishes’ health and reproduction, as well as for human health. In the specific work, three major categories of contaminants, pesticides, pharmaceuticals, and macro and trace elements, were investigated in two major fish species, [...] Read more.
The monitoring of contaminants in fish species is pivotal for fishes’ health and reproduction, as well as for human health. In the specific work, three major categories of contaminants, pesticides, pharmaceuticals, and macro and trace elements, were investigated in two major fish species, Dicentrarchus labrax and Solea solea, collected from Thermaikos Gulf, in Greece. To achieve this goal, three analytical methods using LC-MS/MS, GC-MS/MS, and ICP-MS were developed, validated, and applied to the collected fish samples. The results indicated a very low prevalence of caffeine and acetaminophen, both not exceeding 3.8 μg/kg fish. Similarly, thiabendazole, cypermethrin, and tricyclazole (pesticides) were found in a concentration range of 0.9 to 13.7 μg/kg fish, while in one D. labrax sample, traces of the metabolite of organochlorine pesticide DDT, o,p’-DDE were detected. Al, Mn, Fe, Zn, and Sr were the predominant trace elements in a concentration range of 500–20,000 μg/kg fish. Macro elements levels varied from 280 to 5405 mg/kg fish. Health risk assessment did not unveil an unacceptable risk for the human health of adults, apart from one sample presenting Hg above the regulatory levels. On the contrary, for children, the calculated hazard quotient values for Hg in all cases and for two As detections were higher than the threshold value of 1, indicating a potential risk. Full article
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Figure 1

Figure 1
<p>Map of sampling points (photo retrieved from Google Maps).</p>
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<p>MRM chromatograms of cypermethrin (as a sum of cis and trans diastereomers) in a positive sample.</p>
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<p>MRM chromatograms of caffeine in a positive sample.</p>
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<p>Box plots of the most abundant trace elements (Al, Mn, Fe, Zn, Sr) concentration (μg/Kg) in <span class="html-italic">D. larbax</span> (<span class="html-italic">n</span> = 5) and <span class="html-italic">S. solea</span> (<span class="html-italic">n</span> = 5) fish samples.</p>
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<p>Box plots of macro elements concentration (mg/Kg) in <span class="html-italic">D. larbax</span> (<span class="html-italic">n</span> = 5) and <span class="html-italic">S. solea</span> (<span class="html-italic">n</span> = 5) fish samples.</p>
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<p>Βox plots of toxic elements concentration (μg/Kg) in <span class="html-italic">D. larbax</span> (<span class="html-italic">n</span> = 5) and <span class="html-italic">S. solea</span> (<span class="html-italic">n</span> = 5) fish samples. Cd concentrations are not included, since they were all below LOQ value.</p>
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