| Literature DB >> 35447773 |
Li-Na Sun1, Xiu-Jing Shen2, Li-Jun Cao2, Jin-Cui Chen2, Li-Jun Ma2, San-An Wu1, Ary Anthony Hoffmann3,4, Shu-Jun Wei2.
Abstract
The western flower thrips Frankliniella occidentalis (Pergande) (Thysanoptera: Thripidae) is an important invasive pest worldwide. Field-evolved resistance to the pesticide spinetoram is an increasing problem in the chemical control of this pest. Here, we examined changes in the frequency of a genetic mutation associated with spinetoram resistance, the G275E mutation in the acetylcholine receptor Foα6, in 62 field populations collected from 2009 to 2021 across areas of China invaded by this pest. We found a low frequency of the G275E mutation in populations collected at the early invasion stage, in contrast to a high frequency in native USA populations. However, the frequency of the G275E mutation has increased to a high level in recently collected populations, with the mutation becoming fixed in some populations. There was a correlation between the frequency of the G275E mutation and resistance to spinetoram as characterized by median lethal concentration, although two populations were outliers. These results showed that G275E mutation is one of the mechanisms conferring spinetoram resistance in many invading populations in China. Ongoing dispersal of the WFT may have facilitated a rapid increase in the G275E mutation across China. Our study highlights the rapid evolution of pesticide resistance in an invasive species and points to a useful marker for molecular diagnostics of spinetoram resistance.Entities:
Keywords: KASP; biological invasion; molecular diagnostics; pesticide resistance; spinosyns
Year: 2022 PMID: 35447773 PMCID: PMC9029678 DOI: 10.3390/insects13040331
Source DB: PubMed Journal: Insects ISSN: 2075-4450 Impact factor: 2.769
Figure 1Sample locations (red triangle) of Frankliniella occidentalis populations collected in (a) 2009–2013, (b) 2014–2018 and (c) 2020–2021. The larger red triangle represents multiple populations collected from Beijing.
Regressions for spinetoram responses and frequencies of G275E R/S genotypes in seven Frankliniella occidentalis populations.
| Population | Year | Toxicity Regression | LC50 (95% CI) (mg·L−1) * | SE (of b) |
| RR | R% | RR% | RS% | |
|---|---|---|---|---|---|---|---|---|---|---|
| BJDJ | 2017 | 2.76x + 6.73 | 0.24 (0.18–0.30) D | 0.4399 | 0.5755 | 0.9020 | 1 | 2.2 | 0 | 4.5 |
| BJDQ | 2020 | 2.07x + 4.28 | 42.32 (35.82–50.19) A | 0.1941 | 0.4737 | 0.9246 | 176.33 | 47.2 | 39.1 | 16.3 |
| BJPG | 2020 | 2.45x + 5.23 | 0.81 (0.62–1.04) BC | 0.3847 | 1.4003 | 0.4965 | 3.38 | 17.2 | 10.3 | 13.8 |
| BJDJ | 2020 | 2.45x + 0.78 | 52.90 (43.87–64.28) A | 0.2954 | 9.4655 | 0.0237 | 220.42 | 14.3 | 0 | 28.6 |
| BJTZ | 2020 | 3.35x + 4.90 | 1.07 (0.92–1.30) B | 0.3627 | 0.4164 | 0.8120 | 4.46 | 15.9 | 0 | 31.8 |
| BJDS | 2021 | 2.13x + 5.40 | 0.65 (0.47–0.84) C | 0.2250 | 9.4401 | 0.0510 | 2.71 | 4.6 | 0 | 9.1 |
| BJHD | 2021 | 0.91x + 4.15 | 8.70 (3.91–54.323) A | 0.1078 | 19.1711 | 0.0018 | 36.25 | 1.6 | 0 | 3.3 |
SE, standard error; RR, resistance ratio. * Differences in LC50 were considered significant when the 95% CIs did not overlap, and these are marked by different letters.
Figure 2Genotype frequencies of G275E mutation in Frankliniella occidentalis populations during (a) 2009–2013, (b) 2014–2018 and (c) 2020–2021. RR, resistant homozygote genotype; RS, heterozygote genotype; SS, sensitive homozygote genotype. The “*” represents deviations from Hardy-Weinberg equilibrium (p < 0.05); NA represents a population consisting only of homozygous genotypes.
Figure 3Plot of G275E-resistant allele frequencies in three collecting periods. The horizontal black solid line represents the median for each period; the red dot represents the mean. Red error bars indicate the standard error.
Figure 4Regression between (ln) LC50 and the frequencies of (a) the resistant allele, (b) RR resistant genotype and (c) the sum of homozygous and heterozygote genotypes with the resistant G275E mutation across all populations tested. We have also provided the regressions when the BJDJ2020 and BJHD2021 populations are excluded (d–f).