| Literature DB >> 35897869 |
Min-Ting Tu1, Ying-Ying Shao1, Sen Yang1, Bin-Long Sun1, Ying-Ying Wang1, Cheng-Xia Tan1, Xue-Dong Wang2.
Abstract
In order to discover pesticidal lead compounds with high activity and low toxicity, a series of novel benzamides substituted with pyrazole-linked 1,2,4-oxadiazole were designed via bioisosterism. The chemical structures of the target compounds were confirmed via 1H NMR, 13C NMR and HRMS analysis. The preliminary bioassay showed that most compounds exhibited good lethal activities against Mythimna separate, Helicoverpa armigera, Ostrinia nubilalis and Spodoptera frugiperda at 500 mg/L. Particularly in the case of Mythimna separate, compound 14q (70%) exhibited obvious insecticidal activity. In addition, compound 14h demonstrated good fungicidal activity against Pyricularia oryae with an inhibition rate of 77.8%, and compounds 14e, 14k, 14n and 14r also showed certain antifungal activities (55.6-66.7%). The zebrafish toxicity test showed that the LC50 of compound 14h was 14.01 mg/L, which indicated that it may be used as a potential leading compound for further structural optimization.Entities:
Keywords: 1,2,4-oxadiazole; benzamide compounds; biological activity; pyrazole; synthesis
Mesh:
Substances:
Year: 2022 PMID: 35897869 PMCID: PMC9330712 DOI: 10.3390/molecules27154692
Source DB: PubMed Journal: Molecules ISSN: 1420-3049 Impact factor: 4.927
Figure 1Chemical structures of tebufenpyrad, penflufen, chlorantraniliprole, penthiopyrad, cyantraniliprole and sedaxane.
Figure 2Design strategy for the target compounds.
Scheme 1Synthetic route of target compounds 14.
Scheme 2The Knorr cyclization reaction of compound 3, performed under high temperature.
Insecticidal activities of compounds 14a–14s.
| Compounds | R | Insecticidal Activities (Death Rates %) | ||||
|---|---|---|---|---|---|---|
|
| H | 50 | 20 | 10 | 0 | 10 |
|
| 2-CH3 | 20 | 10 | 5 | 10 | 0 |
|
| 3-CH3 | 30 | 10 | 10 | 5 | 25 |
|
| 4-CH3 | 10 | 15 | 30 | 0 | 0 |
|
| 4-t-Bu | 20 | 25 | 40 | 0 | 5 |
|
| 3-CF3 | 50 | 35 | 50 | 15 | 20 |
|
| 2-F | 25 | 30 | 45 | 0 | 5 |
|
| 3-F | 30 | 35 | 50 | 20 | 0 |
|
| 4-F | 35 | 20 | 30 | 70 | 30 |
|
| 2-Cl | 15 | 25 | 40 | 25 | 0 |
|
| 3-Cl | 40 | 10 | 0 | 10 | 15 |
|
| 4-Cl | 30 | 15 | 20 | 30 | 5 |
|
| 4-Br | 5 | 0 | 0 | 0 | 0 |
|
| 4-I | 20 | 10 | 5 | 0 | 10 |
|
| 2,4-di-CH3 | 10 | 15 | 15 | 20 | 25 |
|
| 2,6-di-CH3 | 20 | 15 | 10 | 30 | 0 |
|
| 3-Cl-2-CH3 | 70 | 45 | 15 | 40 | 25 |
|
| 3,4-di-Cl | 40 | 10 | 5 | 10 | 0 |
|
| 2,4-di-F | 50 | 20 | 10 | 0 | 15 |
| Tebufenpyrad | 60 | 45 | 40 | 30 | 45 | |
Note: All the data were determined three times.
Fungicidal activities of compounds 14a–14s at 50 mg/L.
| Compounds | R | Fungicidal Activities (Inhibition Rate %) | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
|
|
|
|
|
|
|
|
|
| ||
|
| H | 21.4 | 17.6 | 33.3 | 18.8 | 16.1 | 11.4 | 24.4 | 17.4 | 13.3 | 19.4 |
|
| 2-CH3 | 21.4 | 26.5 | 22.2 | 9.4 | 29.0 | 13.6 | 22.0 | 8.7 | 6.7 | 8.3 |
|
| 3-CH3 | 21.4 | 32.4 | 55.6 | 18.8 | 32.3 | 18.2 | 4.9 | 8.7 | 20.0 | 25.0 |
|
| 4-CH3 | 28.6 | 44.1 | 44.4 | 18.8 | 9.7 | 4.5 | 12.2 | 17.4 | 13.3 | 8.3 |
|
| 4-t-Bu | 21.4 | 38.2 | 55.6 | 12.5 | 16.1 | 18.2 | 4.9 | 8.7 | 6.7 | 8.3 |
|
| 3-CF3 | 21.4 | 23.5 | 11.1 | 12.5 | 29.0 | 22.7 | 7.3 | 8.7 | 6.7 | 11.1 |
|
| 2-F | 21.4 | 23.5 | 33.3 | 9.4 | 45.2 | 13.6 | 22.0 | 8.7 | 40.0 | 11.1 |
|
| 3-F | 21.4 | 35.3 | 77.8 | 3.1 | 38.7 | 13.6 | 4.9 | 8.7 | 6.7 | 2.8 |
|
| 4-F | 7.1 | 44.1 | 33.3 | 3.1 | 32.3 | 18.2 | 12.2 | 8.7 | 26.7 | 30.6 |
|
| 2-Cl | 21.4 | 14.7 | 44.4 | 3.1 | 41.9 | 22.7 | 36.6 | 4.3 | 40.0 | 33.3 |
|
| 3-Cl | 14.3 | 35.3 | 66.7 | 12.5 | 38.7 | 13.6 | 4.9 | 4.3 | 6.7 | 13.9 |
|
| 4-Cl | 14.3 | 32.4 | 11.1 | 12.5 | 32.3 | 18.2 | 36.6 | 4.3 | 33.3 | 11.1 |
|
| 4-Br | 7.1 | 17.6 | 11.1 | 12.5 | 38.7 | 13.6 | 12.2 | 4.3 | 26.7 | 30.6 |
|
| 4-I | 50.0 | 55.9 | 66.7 | 12.5 | 58.1 | 31.8 | 65.9 | 13.0 | 53.3 | 30.6 |
|
| 2,4-di-CH3 | 21.4 | 35.3 | 11.1 | 12.5 | 58.1 | 31.8 | 48.8 | 8.7 | 60.6 | 25.0 |
|
| 2,6-di-CH3 | 28.6 | 38.2 | 33.3 | 9.4 | 51.6 | 27.3 | 4.9 | 8.7 | 46.7 | 22.2 |
|
| 3-Cl-2-CH3 | 21.4 | 32.4 | 44.4 | 18.8 | 48.4 | 40.9 | 31.7 | 4.3 | 40.0 | 22.2 |
|
| 3,4-di-Cl | 21.4 | 17.6 | 55.6 | 9.4 | 25.8 | 31.8 | 24.4 | 8.7 | 6.7 | 11.1 |
|
| 2,4-di-F | 21.4 | 23.5 | 44.4 | 3.1 | 32.3 | 22.7 | 46.3 | 8.7 | 40.0 | 11.1 |
| Bixafen | 92.9 | 70.6 | 100.0 | 40.6 | 100.0 | 72.7 | 92.7 | 73.9 | 86.7 | 77.8 | |
Note: Alternaria solani (AS), Gibberella zeae (GZ), Pyricularia oryae (PO), Phytophthora capsica (PC), Sclerotinia sclerotiorum (SS), Botrytis cinerea (BC), Riziocotinia solani (RS), Fusarium oxysporum (FO), Cercospora arachidicola (CA), Physalospora piricola (PP). All the data were determined three times.
EC50 of compound 14h and bixafen to Pyricularia oryae (PO).
| Compounds | y = a + bx | r2 | EC50/(mg·L−1) |
|---|---|---|---|
|
| y = 1.6022x + 3.0305 | 0.9968 | 16.95 |
| bixafen | y = 1.7973x + 3.2716 | 0.9766 | 9.15 |
Figure 3Zebrafish embryo mortality rates after exposure to 14h.
Figure 4Zebrafish embryo malformation after exposure to compound 14h.