Fifty mungbean germplasms
viz., AKM 4, AKM 12-28, AKM 8802, BM 2019-10, BM 2021-2, BM 4, COGG 912, GJM 1701, SML 1839, IGKM 05-06-27, IGKM 06-10-7, IPM 1205-2, IPM 13-6, IPM 1603-3, IPM 1603-7, IPM 2-14, IPM 2-3, IPM 2K-14-9 (VARSHA), IPM 410-3, IPM 512-1, JLPM 702-1, JLPM 707-27, K 851, KM 2417, LGG 610, LGG 628, MGG 519, MH 1908, MH 1142, MH 1772, MH 1857, MH 2-15, MI 750-1, MI 98-64, ML 2506, ML 2738, ML 818, ML 2748, OBGG 104, OBGG 106, OBGG 112, OUM 11-5, PM 1903, PM 1711, PM 1723, PM 1918, PM 6, PM 4, PMS 8 and PUSA 0672 were screened for significant insect pests in two successive crop seasons under field conditions
i.
e.,
Kharif 2022 and 2023. The frequency of the major insect pests from crop seeding to pre-harvest was monitored every week. The information gathered during the testing period on various insect pests is given as follow.
Whitefly, Bemisia tabaci (Gennadius)
The population of whitefly was recorded on all 50 mungbean germplasm during
Kharif 2022 and 2023 to see the performance of germplasms based on the level of infestation of whitefly. The whitefly/cage varied from 3.4 to 5.9, 2.6 to 4.6 and 3.0-5.6 during
Kharif 2022, 2023 and in pooled data of both the year, respectively. During
Kharif 2022, the whitefly population was minimum in MI 98-64 (3.4 whitefly/cage) followed by JLPM 702-1, IPM 410-3 and IPM 512-1 (3.4, 3.6, 3.7 and 3.7 whitefly/cage, respectively) and maximum in PM 1723 (6.6 whitefly/cage) (Table 1). In the 2nd year of evaluation, whitefly population was minimum in JLPM 702-1 and MI 98-64 (2.6 whitefly/cage) followed by IGKM 05-06-27 and MH 1908 (2.8 whitefly/cage). Maximum whitefly population was noticed in germplasm BM 4, ML 818, PM 1723 (4.6 whitefly/cage) (Table 2). The whitefly population was minimum in MI 98-64 (3.0 whitefly/cage) followed by JLPM 702-1 (3.1 whitefly/cage) and maximum in ML818 and PM 1723 (5.6 whitefly/cage) in the combined data for both years (Table 3).
The pre sent study is supported by
Chauhan et al., (2018) who observed that the white fly population varied from 3.66 to 23.30 whiteflies/cage after screening 50 mungbean germplasm samples. The highest reported whitefly population, according to the data, was found in germplasm RMG-1092 (23.30 whiteflies per cage). This was followed by AKM 12-14 and GAM-5 (13.66 whiteflies per cage), Pant M-6 (13.33 whiteflies per cage), PM 11-25 (12.66 whiteflies per cage) and LGG 450 (11.66 whiteflies per cage). But the lowest population was noted in GM 11-02 and MDGVV 16 (3.66 white flies per cage), then TMB 1343 (4.00 white flies per cage), ML 2410 and IPM 312-9 (4.33 white flies per cage). The susceptibility and resistance of fifty mungbean germplasm to
Bemisia tabaci is also examined by
Singh et al., (2019). Not a single germplasm was discovered to be free of the white fly population, either at the 50% blooming or 50% pod maturity stages. In genotypes SUM 14-7 (2.50 whiteflies per plant) and NDM 97-2 (1.95 whiteflies per plant), the maximum whitefly populations at 50% blooming and 50% pod maturity stages were found, respectively. KM 13-47, PUSA 0672, PUSA 0871, PUSA 1331, PUSA 1332, PUSA 1441and PUSA 9531 were among the germplasm that did, however, exhibit resistance against whitefly.
Jassid, Empoasca kerri (Pruthi)
Based on data from Table 1, it was found that during
Kharif 2022, the number of jassid fluctuated between 0.4 and 3.3 per cage. Germplasm KM 2417 had the lowest jassid population (0.4 jassid/cage), followed by LGG 610, PM 4and PUSA 0672 (0.6 jassid/cage). Germplasm IPM 410-3 had the highest population (3.3 jassid/cage), followed by IPM 2K-14-9 (VARSHA) (3.1 jassid/cage). The lowest reported jassid population in
Kharif 2023 was 0.6 jassid/cage in PM 4, whereas the highest population was 2.5 jassid/cage in IPM 410-3 (Table 2). According to the pooled data from both years, the population of jassoids was highest in IPM 410-3 (2.9) and lowest in KM 2417 and PM 4 (0.6) (Table 3).
Chauhan et al., (2018) give credence to the present findings and observed that the jassid population ranged from 7.33 to 30.00 insects/cage. IPM 99-125 (26.33 jassid/cage), Samrat (27.33 jassid/cage), COGG-912 (28.00 jassid/cage), MVL 825 (26.00 jassid/cage) and PUSA 672 (26.00 jassid/cage) were the next five germplasms with the highest reported jassid population (30.00 jassid/cage). PUSA 1672 (7.33 jassid/cage) had the lowest population, while IPM 02-3 (8.00 jassid/cage), MDGVV (8.00 jassid/cage), NVL 516 (10.33 jassid/cage), SKNM 12-06 (11.00 jassid/cage)and AKM 12-14 (11.33 jassid/cage) had the next lowest populations.
Thrips, Caliothrips indicus (Begnall)
The thrips population per five flower buds varied from 0.00 to 1.21, 0.00 to 1.01 and 0.00-1.11 during
Kharif, 2022, 2023 and in pooled data, respectively. During
Kharif, 2022, germplasm COGG 912, IPM 1603-7, IPM 2K-14-9 (VARSHA), PM 1723 and PM 1918 were free from thrips infestation while lowest population was recorded in IPM 410-3 (0.11 thrips/5 flower buds) and maximum in AKM 12-28 (1.21 thrips/5 flower buds) (Table 1). During
Kharif, 2023, the thrips population was not found in germplasm IPM 1603-7, KM 2417 and PM 1723, while, minimum in COGG 912 and PM 6 (0.29 thrips/5 flower buds) and maximum in AKM 12-28 (1.01 thrips/5 flower buds) (Table 2). Pooled data of both the year presented in Table 3 showed that germplasm IPM 1603-7 and PM 1723 were free from thrips while highest population was recorded in AKM 12-28 (1.11 thrips/5 flower buds).
The current study is endorsed by
Chauhan et al., (2018) who noted that there were 8.80 thrips per 5 plants in IGKM 06-26-5. This was followed by 8.70 thrips per 5 plants in NKM 15-12, 8.60 thrips per 5 plants in VGG 10-008, 8.20 thrips per 5 plants in RMG 1092 and 8.00 thrips per 5 plants in Pant M 4. Though the NBPGR-150 recorded the lowest thrip population (3.80 thrips/5 plants), GAM 5 (4.00 thrips/5 plants), NVL 516 (4.20 thrips/5 plants), NVL 825 (4.20 thrips/5 plants), AKM 12-24 (4.20 thrips/5 plants) and Pusa 1672 (4.20 thrips/5 plants) were the next highest populations.
Per cent pod borer damage
The pod borer damage percentage varied from 1.2 to 13.3, 4.0 to 14.1 and 2.7 to 11.5 per cent during
Kharif, 2022, 2023 and in pooled respectively. During
Kharif, 2022, the pod borer damage was minimum in BM 2021-2 (1.2%) followed by IPM 2-3 (1.3%) and ML 2738 (1.4%). Maximum damage was recorded in PUSA 0672 (13.3%) followed by IPM 1205-2 (13%) (Table 1). In the 2nd year of evaluation, pod borer damage was minimum in ML 2738 (4.0%) and maximum in BM 4 (14.1%) (Table 2). Both year’s pooled data revealed that pod borer damage per cent was minimum on ML 2738 (2.7%) followed by MI 98-64 (3.6%) and IPM 2-3 (3.8%), while maximum damage was recorded in K 851 (11.5%) followed by PUSA 0672 (11.4%) and AKM 8802 (11.3%) (Table 3).
Present findings are in partial agreement with the findings of
Kol et al., (2022) who disclosed that the range of pod damage percentages was 1.0% to 14.0%. Out of all the germplasm that was tested, germplasm BM-4 had the least amount of pod damage caused by
M.
vitrata, at 1.00 percent. This was found to be comparable to ML 2500, which had 1.00 per cent pod damage, MH 1142, which had 2.5 per cent pod damage, BCM 18-1, IPM 1604 - 1, IPMD 1603 - 7 and Kopergoan, which had 2.5 per cent pod damage, respectively. Whereas the maximum pod damage was observed in OBGG 104 with 14.00 per cent.
Rani et al., (2014) additionally, it was discovered that
M.
vitrata preferred five genotypes: KM-9- 128; KM-9- 136; RMG-492; LGG-527; and LGG-538 were found to be tolerant; on the other hand, the susceptibility of the other twenty-one genotypes ranged from 12.59 per cent (MGG-332) to 20.0 per cent (IPM-02-03 and LGG-522)and thirteen genotypes were highly susceptible, ranging from 43.25 per cent (KM - 8 - 662). The others ranged from 20.21 per cent (UPM - 99 - 3) to 40.0 per cent (KM - 2241), which indicated how fragile they were.