| Literature DB >> 30717498 |
Qi-Bo Li1, Min Liao2, Qing Liu3, Tong Feng4, Zhi-Yuan Xu5, Chang-Hui Rui6, Shang-Zhong Liu7.
Abstract
New 1,3,5-trimethylpyrazole-containing malonamide derivatives based on pyflubumide were designed, synthesized, and characterized using ¹H-NMR, 13C-NMR, and high-resolution mass spectra (HRMS). The results of preliminary bioassays showed that the target compounds possessed good activities against Tetranychus cinnabarinus, Plutella xylostella, and Aphis craccivora. Most of the target compounds exhibited moderate to good acaricidal activity against Tetranychus cinnabarinus at a concentration of 400 µg/mL, and some showed moderate activity at a concentration of 200 µg/mL; in particular, compounds 8m and 8p exhibited 70.0% mortality. In addition, some of the target compounds exhibited good insecticidal activities against Plutella xylostella at a concentration of 200 µg/mL, especially compounds 8i and 8o, which achieved 100.0% mortality at a concentration of 100 µg/mL. Interestingly, some of the target compounds exhibited potent anti-aphid activity against Aphis craccivora at a concentration of 200 µg/mL; furthermore, compounds 8p and 8q demonstrated 100.0% anti-aphid activity at a concentration of 50 µg/mL. The preliminary analyses of the structure⁻activity relationships (SAR) indicated that the acaricidal and insecticidal activities varied significantly depending on the type of substituent and substitution pattern, which provides guidance for the further investigation of such structural modifications.Entities:
Keywords: acaricidal and insecticidal activities; malonamide; pyflubumide; synthesis
Mesh:
Substances:
Year: 2019 PMID: 30717498 PMCID: PMC6385117 DOI: 10.3390/molecules24030562
Source DB: PubMed Journal: Molecules ISSN: 1420-3049 Impact factor: 4.411
Figure 1Structures of flubendiamide (A), chlorantraniliprole (B), isofetamid (C), and fluopyram (D).
Figure 2The design of the target compounds.
Scheme 1General synthetic route for compounds 8a–8t. Reagents and conditions: (a) Et3N, CH2Cl2, 0–5 °C; (b) LiOH, H2O, THF, 0–25 °C; (c) DCC, CH2Cl2, 0–25 °C; (d) KTB, NMP, 0–25 °C.
Insecticidal activities of compounds 8a~8t and fenpyroximate (FEN) against Tetranychus cinnabarinus.
| Compound | Mortality (%) a | LC50 (µg/mL) | 95% CL (µg/mL) | ||||
|---|---|---|---|---|---|---|---|
| 400 µg/mL | 200 µg/mL | 100 µg/mL | 50 µg/mL | 20 µg/mL | |||
|
| 90.0 ± 3.3 b | 60.0 ± 5.8 | 24.4 ± 1.9 | 11.1 ± 1.9 | 0.0 ± 0.0 | 157.2 | 127.5–197.0 |
|
| 85.6 ± 1.9 | 42.2 ± 1.9 | 20.0 ± 0.0 | 7.8 ± 1.9 | 0.0 ± 0.0 | 197.1 | 158.7–254.9 |
|
| 60.0 ± 3.3 | 35.6 ± 1.9 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 308.8 | 254.2–405.3 |
|
| 61.1 ± 3.8 | 21.1 ± 1.9 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 333.1 | 278.5–431.0 |
|
| 31.1 ± 1.9 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 540.4 | 414.6–1988.6 |
|
| 68.9 ± 3.8 | 31.1 ± 1.9 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 290.7 | 244.6–360.1 |
|
| 51.1 ± 3.8 | 20.0 ± 3.3 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 376.7 | 305.6–544.9 |
|
| 78.9 ± 3.8 | 41.1 ± 1.9 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 250.7 | 212.9–298.7 |
|
| 100.0 ± 0.0 | 64.4 ± 1.9 | 30.0 ± 3.3 | 17.8 ± 1.9 | 7.8 ± 1.9 | 119.2 | 52.0–343.6 |
|
| 90.0 ± 3.3 | 54.4 ± 1.9 | 20.0 ± 3.3 | 7.8 ± 1.9 | 0.0 ± 0.0 | 172.2 | 140.8–214.8 |
|
| 100.0 ± 0.0 | 60.0 ± 3.3 | 20.0 ± 0.0 | 8.9 ± 1.9 | 0.0 ± 0.0 | 149.5 | 124.8–180.9 |
|
| 83.3 ± 3.3 | 51.1 ± 1.9 | 20.0 ± 5.8 | 5.6 ± 1.9 | 0.0 ± 0.0 | 190.9 | 154.8–242.8 |
|
| 90.0 ± 0.0 | 70.0 ± 3.3 | 35.6 ± 1.9 | 27.8 ± 1.9 | 13.3 ± 3.3 | 107.2 | 79.9–145.5 |
|
| 100.0 ± 0.0 | 50.0 ± 3.3 | 20.0 ± 3.3 | 10.0 ± 0.0 | 0.0 ± 0.0 | 158.9 | 84.2–379.2 |
|
| 80.0 ± 3.3 | 40.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 250.3 | 212.9–297.1 |
|
| 100.0 ± 0.0 | 70.0 ± 3.3 | 37.8 ± 1.9 | 15.6 ± 1.9 | 5.6 ± 1.9 | 112.2 | 90.2–140.4 |
|
| 100.0 ± 0.0 | 50.0 ± 3.3 | 20.0 ± 0.0 | 5.6 ± 1.9 | 0.0 ± 0.0 | 164.0 | 103.3–288.0 |
|
| 100.0 ± 0.0 | 60.0 ± 0.0 | 25.6 ± 1.9 | 12.2 ± 1.9 | 7.8 ± 1.9 | 132.3 | 39.7–1172.9 |
|
| 85.6 ± 1.9 | 43.3 ± 3.3 | 20.0 ± 3.3 | 8.9 ± 1.9 | 0.0 ± 0.0 | 194.2 | 156.0–252.1 |
|
| 38.9 ± 1.9 | 18.9 ± 3.8 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 460.3 | 348.5–879.2 |
| FEN | 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | — | — |
a Experimental size: 30 insects per group, three groups. b Each value represents the mean ± standard deviation of three replications; LC50 = 50% lethal concentration; 95% CL = 95% confidence limit; “—” refers to “not calculated”.
Insecticidal activities of compounds 8a–8t and flubendiamide (FLU) against Plutella xylostellas.
| Compound | Mortality (%) a | LC50 (µg/mL) | 95% CL (µg/mL) | ||||
|---|---|---|---|---|---|---|---|
| 400 µg/mL | 200 µg/mL | 100 µg/mL | 50 µg/mL | 20 µg/mL | |||
|
| 80.0 ± 10.0 b | 60.0 ± 0.0 | 30.0 ± 10.0 | 16.7 ± 5.8 | 10.0 ± 0.0 | 153.2 | 89.8–333.2 |
|
| 53.3 ± 5.8 | 30.0 ± 0.0 | 16.7 ± 5.8 | 6.7 ± 5.8 | 0.0 ± 0.0 | 359.0 | 204.7–2371.2 |
|
| 63.3 ± 5.8 | 36.7 ± 5.8 | 10.0 ± 0.0 | 6.7 ± 5.8 | 0.0 ± 0.0 | 289.3 | 183.8–808.9 |
|
| 90.0 ± 0.0 | 73.3 ± 5.8 | 30.0 ± 0.0 | 23.3 ± 5.8 | 16.7 ± 5.8 | 109.5 | 63.0–204.2 |
|
| 100.0 ± 0.0 | 76.7 ± 5.8 | 33.3 ± 5.8 | 26.7 ± 5.8 | 13.3 ± 5.8 | 94.5 | 58.7–153.6 |
|
| 20.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | — | — |
|
| 100.0 ± 0.0 | 100.0 ± 0.0 | 43.3 ± 5.8 | 20.0 ± 0.0 | 6.7 ± 5.8 | 82.6 | 57.2–119.3 |
|
| 86.7 ± 5.8 | 60.0 ± 0.0 | 30.0 ± 10.0 | 13.3 ± 5.8 | 0.0 ± 0.0 | 154.0 | 102.2–250.5 |
|
| 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 83.3 ± 5.8 | 46.7 ± 5.8 | 22.1 | 6.6–33.3 |
|
| 70.0 ± 0.0 | 33.3 ± 5.8 | 20.0 ± 0.0 | 6.7 ± 5.8 | 0.0 ± 0.0 | 257.3 | 164.4–636.1 |
|
| 60.0 ± 0.0 | 50.0 ± 0.0 | 30.0 ± 0.0 | 16.7 ± 5.8 | 6.7 ± 5.8 | 235.4 | 124.0–1322.9 |
|
| 70.0 ± 0.0 | 46.7 ± 5.8 | 26.7 ± 5.8 | 10.0 ± 0.0 | 0.0 ± 0.0 | 93.3 | 57.9–149.3 |
|
| 63.3 ± 5.8 | 30.0 ± 10.0 | 20.0 ± 0.0 | 6.7 ± 5.8 | 0.0 ± 0.0 | 294.2 | 179.9–1000.9 |
|
| 100.0 ± 0.0 | 66.7 ± 5.8 | 40.0 ± 0.0 | 23.3 ± 5.8 | 13.3 ± 5.8 | 99.9 | 61.2–166.9 |
|
| 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 76.7 ± 5.8 | 43.3 ± 5.8 | 24.2 | 8.9–36.5 |
|
| 30.0 ± 0.0 | 10.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 569.8 | 405.6–2013.3 |
|
| 76.7 ± 5.8 | 40.0 ± 0.0 | 20.0 ± 0.0 | 10.0 ± 0.0 | 0.0 ± 0.0 | 220.0 | 142.9–454.3 |
|
| 56.7 ± 5.8 | 26.7 ± 5.8 | 10.0 ± 0.0 | 6.7 ± 5.8 | 0.0 ± 0.0 | 359.0 | 213.2–1857.2 |
|
| 90.0 ± 0.0 | 56.7 ± 5.8 | 26.7 ± 5.8 | 13.3 ± 5.8 | 6.7 ± 5.8 | 149.9 | 95.6–268.6 |
|
| 30.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | — | — |
| FLU | 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ±0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | — | — |
a Experimental size: 10 insects per group, three groups. b Each value represents the mean ± standard deviation of three replications; LC50 = 50% lethal concentration; 95% CL = 95% confidence limit; “—” refers to “not calculated”.
Insecticidal activities of compounds 8a~8t and imidacloprid (IMI) against Aphis craccivora.
| Compound | Mortality (%) a | LC50 (µg/mL) | 95% CL (µg/mL) | ||||
|---|---|---|---|---|---|---|---|
| 200 µg/mL | 100 µg/mL | 50 µg/mL | 20 µg/mL | 10 µg/mL | |||
|
| 100.0 ± 0.0 b | 100.0 ± 0.0 | 80.0 ± 0.0 | 56.7 ± 2.9 | 21.7 ± 2.9 | 19.1 | 13.5–25.4 |
|
| 100.0 ± 0.0 | 100.0 ± 0.0 | 70.0 ± 0.0 | 43.3 ± 2.9 | 20.0 ± 5.0 | 23.3 | 16.8–31.1 |
|
| 100.0 ± 0.0 | 90.0 ± 0.0 | 65.0 ± 0.0 | 36.7 ± 2.9 | 15.0 ± 0.0 | 29.0 | 20.8–39.1 |
|
| 71.7 ± 2.9 | 45.0 ± 0.0 | 20.0 ± 0.0 | 13.3 ± 2.9 | 8.3 ± 2.9 | 111.7 | 73.0–224.0 |
|
| 40.0 ± 0.0 | 20.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 225.3 | 162.9–612.0 |
|
| 100.0 ± 0.0 | 81.7 ± 2.9 | 58.3 ± 2.9 | 31.7 ± 2.9 | 18.3 ± 2.9 | 32.6 | 22.7–45.1 |
|
| 90.0 ± 0.0 | 70.0 ± 0.0 | 50.0 ± 5.0 | 26.7 ± 2.9 | 11.7 ± 2.9 | 46.6 | 32.0–68.0 |
|
| 80.0 ± 5.0 | 50.0 ± 5.0 | 30.0 ± 0.0 | 13.3 ± 2.9 | 8.3 ± 2.9 | 85.0 | 58.3–141.1 |
|
| 100.0 ± 0.0 | 75.0 ± 5.0 | 50.0 ± 0.0 | 28.3 ± 5.8 | 16.7 ± 2.9 | 38.3 | 26.8–53.7 |
|
| 100.0 ± 0.0 | 91.7 ± 2.9 | 60.0 ± 5.0 | 36.7 ± 2.9 | 21.7 ± 2.9 | 27.6 | 19.2–37.9 |
|
| 100.0 ± 0.0 | 100.0 ± 0.0 | 76.7 ± 2.9 | 41.7 ± 2.9 | 25.0 ± 0.0 | 21.4 | 15.2–28.5 |
|
| 71.7 ± 2.9 | 50.0 ± 5.0 | 40.0 ± 0.0 | 26.7 ± 2.9 | 13.3 ± 2.9 | 79.2 | 47.6–173.5 |
|
| 100.0 ± 0.0 | 80.0 ± 0.0 | 50.0 ± 5.0 | 30.0 ± 5.0 | 18.3 ± 2.9 | 35.7 | 24.9–49.8 |
|
| 90.0 ± 0.0 | 68.3 ± 2.9 | 50.0 ± 5.0 | 30.0 ± 0.0 | 18.3 ± 2.9 | 42.9 | 27.8–65.3 |
|
| 75.0 ± 0.0 | 50.0 ± 5.0 | 30.0 ± 0.0 | 18.3 ± 2.9 | 10.0 ± 0.0 | 88.4 | 57.7–166.1 |
|
| 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 88.3 ± 2.9 | 63.3 ± 2.9 | 8.1 | 1.8–11.3 |
|
| 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 83.3 ± 2.9 | 63.3 ± 2.9 | 8.1 | 2.1–11.6 |
|
| 100.0 ± 0.0 | 70.0 ± 5.0 | 60.0 ± 0.0 | 43.3 ± 2.9 | 20.0 ± 5.0 | 30.9 | 19.7–44.9 |
|
| 90.0 ± 5.0 | 65.0 ± 5.0 | 45.0 ± 0.0 | 25.0 ± 0.0 | 13.3 ± 2.9 | 50.7 | 34.5–76.0 |
|
| 50.0 ± 5.0 | 30.0 ± 5.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 | 181.2 | 137.8–320.3 |
| IMI | 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | 100.0 ± 0.0 | — | — |
a Experimental size: 20 insects per group, three groups. b Each value represents the mean ± standard deviation of three replications; LC50 = 50% lethal concentration; 95% CL = 95% confidence limit; “—” refers to “not calculated”.