| Literature DB >> 26837840 |
Yallappa Rajashekar1, Ngaihlun Tonsing1, Tourangbam Shantibala1, Javagal R Manjunath2.
Abstract
The phasing out of methyl bromide as a fumigant, resistance problems with phosphine and other fumigants in stored product beetles, and serious concern with human health and environmental safety have triggered the search for alternative biofumigants of plant origin. Despite the identification of a large number of plants that show insecticidal activity, and the diversity of natural products with inherent eco-friendly nature, newer biofumigants of plant origin have eluded discovery. Using a bioassay driven protocol, we have now isolated a bioactive molecule from the root stock of Colocasia esculenta (L.) and characterized it as 2, 3-dimethylmaleic anhydride (3, 4-dimethyl-2, 5-furandione) based on various physico-chemical and spectroscopic techniques (IR, (1)H NMR, (13)C NMR and Mass). The molecule proved to be an efficient biofumigant which is highly toxic to insect pests for stored grains even at very low concentration, but has no adverse effect on seed germination. We finally address the potential for this molecule to become a, effective biofumigant.Entities:
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Year: 2016 PMID: 26837840 PMCID: PMC4738332 DOI: 10.1038/srep20546
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.379
Figure 1Insecticidal activity of the solvent extracts of C. esculenta to S. oryzae in the fumigant bioassay.
The extracts were applied at 100 μl/l (n = 4, error bars. s.e.m.) one-way ANOVA, ***P < 0.001.
Figure 2Molecular structure of 2, 3-Dimethylmaleic anhydride (2, 5-Furandione, 3, 4- dimethyl).
Insecticidal activity of purified compound (2, 3-Dimethylmaleic anhydride) against adults of household and stored- product insects by fumigant toxicity.
| Insect species | LC50 | LC90 | Slope ± SE | Degrees of freedom |
|---|---|---|---|---|
| 28.8 | 0.642 ± 0.080 | 5 | ||
| 4.5 | 0.611 ± 0.141 | 5 | ||
| 3.96 | 0.734 ± 0.076 | 5 | ||
| 6.12 | 0.371 ± 0.030 | 5 | ||
| 7.02 | 0.729 ± 0.081 | 5 | ||
| 6.48 | 0.825± 0.115 | 5 |
aLC50 and LC90 = μg/l.
bValues in parenthesis represent confidence limits (n = 6).
Comparison of insecticidal activity of 2, 3-Dimethylmaleic anhydride with the chemical fumigants.
| Insecticides (Fumigants) | LC50(μg/l) | ||
|---|---|---|---|
| Ethylene dichloride | 0.53 | 0.70 | 0.42 |
| Allyl acetate | 0.56 | 1.09 | 0.91 |
| Ethylformate | 0.65 | 1.12 | 0.72 |
| Phosphine | 8.0 | 9.8 | 7.8 |
| Methyl bromide | 4.0 | 8.4 | 3.6 |
| Dichlorvos | 0.03 | 0.09 | 0.062 |
aLC50 = μg/l.
Comparison of insecticidal activity of 2, 3-Dimethylmaleic anhydride with the natural fumigants.
| Insecticides (Fumigants) | LC50(μg/l) | ||
|---|---|---|---|
| Carvacrol | 15.3 | 17.0 | 14.2 |
| 1,8 Cineole | 33.0 | 47.0 | 31.0 |
| Eugenol | 11.6 | 37.1 | 23.7 |
| Linalool | 27.7 | 49.8 | 39.2 |
| 21.7 | 61.7 | 54.9 | |
| Coumaran | 0.61 | 3.54 | 0.85 |
Mortality (%) of mixed-age cultures of stored-product insects exposed for 24 h and 72 h to purified compound (2, 3-Dimethylmaleic anhydride) of C. esculenta.
| Dosage (μg/l) | % Mortality (Mean±SE)* | |||||
|---|---|---|---|---|---|---|
| 24 h | 72 h | 24 h | 72 h | 24 h | 72 h | |
| 0 (Control) | 3.7 ± 1.1a | 4.9 ± 1.2a | 2.7 ± 0.6a | 3.3 ± 0.2a | 1.5 ± 0.5a | 2.2 ± 0.8a |
| 10 | 14.7 ± 2.3b | 28.3 ± 2.6b | 17.7 ± 1.4b | 24.3 ± 2.6b | 15.5 ± 1.5b | 23.2 ± 2.2b |
| 25 | 34.7 ± 4.1c | 48.3 ± 2.4c | 30.7 ± 3.1c | 46.3 ± 3.6c | 35.5 ± 3.6c | 40.2 ± 2.8c |
| 50 | 64.5 ± 3.7d | 78.9 ± 4.7d | 58.3 ± 2.4d | 72.9 ± 4.8d | 55.8 ± 1.9d | 75.1 ± 2.6d |
| 75 | 84.7 ± 4.6e | 92.3 ± 2.6e | 77.7 ± 2.1e | 90.3 ± 1.6e | 69.5 ± 4.5e | 83.2 ± 2.8e |
| 100 | 98.6 ± 3.5f | 100f | 94.5 ± 1.8f | 100 f | 84.8 ± 3.9f | 100f |
*There were 5 replicates per dose and in untreated controls (50 g infested media per replicate tested). Values followed by different letters within the vertical columns are significantly different (P < 0.05) by Newman-Keuls test.
Grain protection potential of 2, 3-Dimethylmaleic anhydride.
| Dosage (μg/L1) | % Reduction in F1 progeny* | |||||
|---|---|---|---|---|---|---|
| 24 h | 72 h | 24 h | 72 h | 24 h | 72 h | |
| 0 (Control) | 1.1 ± 0.2a | 3.1 ± 0.4a | 2.0 ± 0.4a | 2.8 ± 0.2a | 8.9 ± 1.2a | 6.9 ± 2.4a |
| 10 | 13.1 ± 2.1b | 24.1 ± 1.4b | 28.1 ± 2.9b | 38.2 ± 1.9b | 15.9 ± 4.7b | 20.4 ± 2.7b |
| 25 | 35.3 ± 5.1c | 53.9 ± 1.5c | 40.6±3.4c | 50.6±5.4c | 37.4 ± 5.1c | 47.4 ± 7.2c |
| 50 | 62.3 ± 2.1d | 77.3 ± 2.1d | 55.3 ± 6.6d | 65.5 ± 3.6d | 62.4 ± 5.6d | 82.7 ± 2.6d |
| 75 | 74.5 ± 2.4e | 90.5 ± 4.4e | 63.1 ± 1.9e | 80.2 ± 6.9e | 75.3 ± 1.4e | 91.3 ± 2.4e |
| 100 | 90.5 ± 6.1f | 100f | 77.5 ± 3.9f | 100f | 86.3 ± 3.4f | 100f |
Adult emergence in F1progeny of stored product insects from treated grain.
*There were 5 replicates per dose and in untreated controls (50 g infested media per replicate tested). Values followed by different letters within the vertical columns are significantly different (P < 0.05) by Newman-Keuls test.