| Literature DB >> 35567194 |
Amal Ramzi1, Abdelhakim El Ouali Lalami1,2, Yassine Ez Zoubi1,3, Amine Assouguem1,4, Rafa Almeer5, Agnieszka Najda6, Riaz Ullah7, Sezai Ercisli8, Abdellah Farah1.
Abstract
The present study investigates the insecticidal effect of plant extract such as Mentha pulegium and Rosmarinus officinalis essential oils and some of their major compounds; these plants are well known for their many biological activities. The fumigant toxicity was evaluated, using glass jars, against female adults of Culex pipiens that constitute a mosquito vector of important diseases such as the West Nile virus. The adulticidal test showed that both essential oils and monoterpenes presented an insecticidal effect better than the chemical insecticide (Deltamethrin). The highest mortality percentages for the two essential oils have occurred at 312.5 µL/L air (between 56.14 ± 1.7% and 97.71 ± 3.03% after 24 h and 48 h of treatment). Moreover, all tested monoterpenes (carvone, R(+)-pulegone, 1,8-cineole, camphor and α-pinene) have produced high mortalities that varied depending on the time of the treatment and the concentrations used. Lethal concentrations (LC50) obtained for the essential oils and the main compounds have also varied according to the exposure time. M. pulegium and R. officinalis essential oil exhibited the lowest LC50 values after 24 h (72.94 and 222.82 µL/L air, respectively) and after 48 h (25.43 and 55.79 µL/L air, respectively) while the pure molecules revealed the lowest LC50 values after 48 h (between 84.96 and 578.84 µL/L air). This finding proves that the two essential oils and their main compounds have an insecticidal potential, which could help to develop natural toxic fumigants that may be used as an eco-friendly alternative in integrated and sustainable vector management.Entities:
Keywords: Culex pipiens; Mentha pulegium; Rosmarinus officinalis; essential oils; fumigant toxicity; monoterpenes; mosquitoes
Year: 2022 PMID: 35567194 PMCID: PMC9105606 DOI: 10.3390/plants11091193
Source DB: PubMed Journal: Plants (Basel) ISSN: 2223-7747
The chemical compounds identified in M. pulegium and R. officinalis EOs.
|
|
| RI (Lit) b |
|
|
|---|---|---|---|---|
| α-Thujene | 931 | 924 | - | 0.48 |
|
| 939 | 932 | 0.42 |
|
| Cyclohexanone-3-methyl | 952 | 945 | 0.16 | - |
| Camphene | 953 | 946 | - | 2.47 |
| β-Pinene | 976 | 974 | 0.33 | 2.89 |
| Unknown | 957 | - | - | t |
| Unknown | 958 | - | 0.08 | t |
| Unknown | 961 | - | 0.07 | t |
| Unknown | 985 | - | t | - |
| Myrcene | 993 | 988 | 0.16 | 2.54 |
| Octanol-3 | 993 | 995 | 1.32 | - |
| Unknown | 995 | - | - | t |
| δ-2-Carene | 1001 | 998 | 0.11 | - |
| Unknown | 1023 | - | 0.07 | 1.5 |
| Limonene | 1031 | 1029 | 1.34 | - |
|
| 1033 | 1033 | - |
|
| Unknown | 1035 | - | - | t |
| Unknown | 1040 | - | - | t |
| Unknown | 1064 | - | t | t |
| p-Mentha-3,8-diene | 1071 | 1072 | 2.04 | - |
| Unknown | 1075 | - | t | 1.03 |
| Unknown | 1100 | - | - | t |
|
| 1143 | 1141 | - |
|
| Unknown | 1148 | - | - | t |
| Menthone | 1154 | 1148 | 0.13 | - |
| Borneol | 1165 | 1166 | - | 5.46 |
| Pinocarvone | 1168 | 1160 | 1.21 | - |
| Menthol | 1173 | 1167 | 0.45 | - |
| α-Terpineol | 1185 | 1186 | - | 0.63 |
| Dihydrocarvone | 1194 | 1191 | 3.66 | - |
| Myrtenol | 1195 | 1194 | - | 1.23 |
| Unknown | 1207 | - | 0.09 | - |
|
| 1238 | 1233 |
| - |
|
| 1242 | 1239 |
| - |
| Unknown | 1245 | - | - | 0.2 |
| Peperitone | 1252 | 1249 | 1.12 | - |
| Unknown | 1265 | - | - | 0.2 |
| Myrtenyl acetate | 1322 | 1324 | - | 0.22 |
| α-Cubebene | 1351 | 1345 | - | 0.15 |
| α-Copaene | 1381 | 1374 | - | 0.10 |
| β-Bourbonene | 1384 | 1387 | - | 0.16 |
| Unknown | 1397 | - | 0.06 | - |
| Caryophyllene | 1419 | 1417 | 0.35 | - |
| γ-Gurjunene | 1473 | 1475 | - | 0.2 |
| Germacrene-D | 1480 | 1484 | 0.42 | |
| Ledene | 1493 | 1490 | - | 2.92 |
| α-Muurolene | 1499 | 1500 | - | 0.32 |
| γ-Cadinene | 1513 | 1513 | - | 0.8 |
| Caryophyllene oxide | 1581 | 1582 | - | 2.75 |
| Copaen-4-α-ol | 1584 | 1590 | - | 0.43 |
| Tetradecanal | 1611 | 1612 | - | 0,21 |
| γ-Eudesmol | 1630 | 1630 | 0.26 | - |
| τ.Cadinol | 1653 | 1654 | - | 0.19 |
| α-Eudesmol | 1649 | 1652 | 0.44 | - |
| Total identified compounds | 93.35 | 94.23 |
a: Experimental retention indices. b: Retention indices from literature [30,34]. * The quantity of each compound was given by percentages that were presented as a ratio of the areas of the chromatographic peaks. T: trace < 0.05%. The compounds indicated in bold represent the major constituents, in both EOs, that have been tested for their insecticidal effect.
Figure 1Evaluation of M. pulegium and R. officinalis EOs toxicity on C. pipiens adults according to different concentrations: (A): After 24 h; (B): After 48 h. (*): Positive control (Deltamethrin 0.05%). Means followed by the same letter are not significantly different at p-value (0.05).
Figure 2Toxicity of monoterpenes against C. pipiens adults at various concentrations after 24 h (A), and 48 h (B) of treatment. Results are means of three replicates (n = 3). Bars indicate standard errors. Tests were statistically significant at p-value (0.05).
Lethal concentrations (LC50) of M. pulegium and R. officinalis EOs and their main compounds.
| EOs and Monoterpenes | Exposure Time (h) | LC50
a (µL/L Air) | Slope b | Intercept c | R2 | |
|---|---|---|---|---|---|---|
|
| 24 | 72.94 (60.34–83.32) | 1.146 ± 0.15 | 2.865 ± 0.30 | 0.94 | 0.005 |
| 48 | 25.43 (13.22–38.65) | 1.169 ± 0.18 | 3.357 ± 1.23 | 0.94 | 0.005 | |
|
| 24 | 222.82 (210, 234.29) | 0.957 ± 0.11 | 2.753 ± 0.63 | 0.93 | 0.003 |
| 48 | 55.79 (50.77–60.81) | 1.093 ± 0.08 | 3.091 ± 1.18 | 0.93 | 0.003 | |
|
| 24 | 1713.36 (1703.33–1723.36) | 0.774 ± 0.04 | 2.497 ± 0.12 | 0.96 | 0.000 |
| 48 | 538.96 (512.84–568.36) | 0.827 ± 0.02 | 2.741 ± 0.07 | 0.99 | 0.000 | |
|
| 24 | 5395.58 (5295.58–5494.68) | 0.515 ± 0.01 | 3.078 ± 0.02 | 0.99 | 0.000 |
| 48 | 578.84 (578.24–597.64) | 0.577 ± 0.05 | 3.406 ± 0.14 | 0.93 | 0.000 | |
|
| 24 | 5395.65 (5282.45–5486.55) | 0.362 ± 0.01 | 3.649 ± 0.03 | 0.98 | 0.000 |
| 48 | 84.96 (75.8–95.26) | 0.537 ± 0.05 | 3.964 ± 0.14 | 0.90 | 0.000 | |
|
| 24 | 2269.64 (2190.41–2354.45) | 0.663 ± 0.01 | 2.775 ± 0.04 | 0.98 | 0.000 |
| 48 | 205.38 (167.83–300.51) | 1. 027 ± 0.08 | 2. 6258 ± 0.22 | 0.94 | 0.000 | |
|
| 24 | 1294.64 (1230–1345.14) | 0.642 ± 0.06 | 3.002 ± 0.16 | 0.92 | 0.000 |
| 48 | 85.74 (74.04–98.21) | 0.509 ± 0.01 | 4.016 ± 0.04 | 0.99 | 0.000 |
a: Lethal concentration killing 50% of exposed adult population. b: Slope of the regression line ± SE. c: Intercept of the regression line ± SE. d: Significant effect at p-value < 0.05.