Comparative Evaluation of Selected Biorational Insecticides against Spodoptera litura (Fabricius) on Cauliflower
Comparative Evaluation of Selected Biorational Insecticides against Spodoptera litura (Fabricius) on Cauliflower
Sumaira Maqsood1,*, Muhammad Afzal2, Muhammad Anjum Aqueel2, Waqas Wakil3 and Hafiz Azhar Ali Khan1,*
1Institute of Agricultural Sciences, University of the Punjab, Lahore
2Department of Agriculture Entomology, University College of Agriculture, University of Sargodha
3Institute of Agricultural Sciences, University of the Punjab, Lahore
ABSTRACT
Spodoptera litura is an economic pest of different field crops including cauliflower. In the present study three commercial formulations of biorational insecticides viz., Bacillus thuringiensis (DiPel®), NPV (SpltNPV) and Flubendiamide (Belt®) evaluated (alone and in combination) against S. litura under field condition. Minimum plant infestation (7.60±0.40%) was observed three days after application when B. thuringiensis and flubendiamide were applied in combination (@0.5 kg/ha+75ml/ha, respectively). Maximum infestation (11.60±0.97%) was observed in SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @1.00 kg/ha. Similarly, five days after application minimum plant infestation was observed in B. thuringiensis and flubendiamide @0.5 kg/ha+75ml/ha (5.20±0.49%) and maximum in SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @1.00 kg/ha (8.80±0.49%). Whereas, minimum plant infestation was observed seven days after application where B. thuringiensis and flubendiamide were applied in combination @0.5 kg/ha+75ml/ha i.e. 2.80±0.49 % followed by B. thuringiensis @1.0 kg/ha + flubendiamide 480 SC @ 75ml/ha, SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @0.5 kg/ha, SpltNPV @ 1.0×109 POB/ml + flubendiamide 480 SC @ 75ml/ha and SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @1.00 kg/ha i.e. 4.00±0.63, 4.40±0.40, 4.80±0.48 and 5.60±0.40 %, respectively. Whereas, B. thuringiensis @1.0 kg/ha, flubendiamide @ 75ml/ha, SpltNPV @ 1.0×109 POB/ml and B. thuringiensis @0.5 kg/ha were gave plant infestation 6.40±0.40, 6.80±0.49, 8.80±0.48 and 9.20±0.49%, respectively. After second application, lowest plant infestation was recorded in the plot treated with B. thuringiensis @0.5 kg/ha+ flubendiamide 480SC @75ml/ha with plant infestation of 8.40±0.40, 5.60±0.40 and 2.20±0.40 % at three, five and seven days after application, respectively. However, all the insecticides reduced natural enemies (Chrysoperla carnea, ladybird beetles, and predatory bugs) populations in all the treatments. In conclusion, the results revealed the potential of Bt, NPV and flubendiamide for the management of S. litura. Further studies are needed to confirm the potential of these products against S. litura and negative impact on natural enemies under varying climatic conditions, and on different host crops.
Article Information
Received 11 January 2018
Revised 20 March 2018
Accepted 04 May 2018
Available online 30 July 2018
Authors’ Contribution
SM performed the study, analyzed the data and wrote the manuscript. MA, MAA and WW designed and supervised the study. HAAK helped in the data analysis and writing of the manuscript.
Key words
Microbial insecticide, Ecotoxicology, Insect-pest management.
DOI: http://dx.doi.org/10.17582/journal.pjz/2018.50.5.1645.1652
* Corresponding authors: azhar.iags@pu.edu.pk;
sumaira.ento@yahoo.com
This article is a part of PhD thesis of first author
0030-9923/2018/0005-1645 $ 9.00/0
Copyright 2018 Zoological Society of Pakistan
Introduction
Cauliflower (Brassica oleracea var. botrytis) is an important crop grown in South-East Asia. It is used as a vegetable as well as in different kinds of salads, throughout the year in homes and hotels of Pakistan. It is damaged by a large number of insect pests; of these, armyworm (Spodoptera litura F.) is one of the most serious pests causing yield losses ranging from 31% to 100%. It invades more than 40 plant families (Lingappa et al., 2004). The status of S. litura is an admitted fact as a major pest of cauliflower crop. Spodoptera litura being an allopatric species is widely reported in Asia and other continents. It is a highly cosmopolitan and polyphagous pest which invades a wide host range of agricultural crops (Singh et al., 2015). Based on the crop damages, it is also known as Indian leaf worm, tobacco caterpillar and tobacco cutworm. Severe incidence of this pest may demand wide use of insecticides to safeguard the infested crops (Carasi et al., 2014).
Populations of S. litura in Pakistan have developed broad-spectrum resistance against conventional (chlorinated hydrocarbons, organophosphates, carbamates and pyrethroids) and newer chemistry insecticides (spinosad, indoxacarb, fipronil, avermectins and insect growth regulators) (Abbas et al., 2012). Literature ensures its prime importance as first lepidopterous pest to develop insecticidal resistance in India (Srivastava and Joshi, 1965). Concerns related to human environment and development of resistance have inspired the researchers to investigate alternative options to conventional chemical application (Carlton and Gonzalez, 1986; Brousseau et al., 1998). Now the pest management efforts are directed towards the use of bio-pesticides because of their promising potential for protection of economically important agricultural crops and environment (Nguyen, 2007; Inglis et al., 2010).
In Pakistan, the use of conventional insecticides has been the major choice to manage different insect pests of economic importance which ultimately lead to evolve insecticide resistance and field control failures (Khan et al., 2016a, b). Biorational insecticides are very effective tool to manage the resistance problems and protect natural enemies and environment (Khan and Akram, 2017; Yasoob et al., 2017). These insecticides are very effective against the target pests but less detrimental to natural enemies. Theses pesticides are usually derived from biologically active substances like plants and microbes that affect the growth and development of insects and provide protection against herbivores including lepidopteran pests (Senthil et al., 2005; Ignacimuthu et al. 2006; Baskar et al., 2011).
The main objective of this study was to check the efficacy of commercial formulations of NPV, Bt and flubendiamide alone and in different combinations against S. litura under field conditions.
Materials and methods
The experiment was carried out under field conditions on cauliflower crop grown in the Faisalabad region (Chak No. 208/R.B.).
Cauliflower nursery plants were transplanted in furrows following the randomized complete block design (RCBD) with four replications. All the recommended agronomic practices were undertaken for the purpose to gain healthy plants. Two spray applications, each with four replicates, of three bio-rational formulations, including flubendiamide (Belt), B. thurengiensis (DiPel) and NPV (SpltNPV) were carried out against S. litura. Data regarding %age plant infestation were recorded from 25 plants in each replication at three, five and seven days after application. While, the data regarding natural enemies’ population (Chrysoperla carnea, ladybird beetle and predatory bugs) were also recorded from 25 randomly selected plants per replication at three, five and seven days after application. Whereas, mortality of S. litura caused by the application of insecticides was also recorded at the same time intervals. Following treatments were applied: T1, B. thuringiensis @0.5 kg/ha; T2, B. thuringiensis @1.0 kg/ha; T3, SpltNPV @ 1.0×109 POB/ml; T4, flubendiamide 480 SC @ 75ml/ha; T5, SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @0.5 kg/ha; T6, SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @1.00 kg/ha; T7, SpltNPV @ 1.0×109 POB/ml + flubendiamide 480 SC @ 75ml/ha; T8, B. thuringiensis @0.5 kg/ha + flubendiamide @ 480 SC @ 75ml/ha; T9, B. thuringiensis @1.0 kg/ha + flubendiamide @480 SC @ 75ml/ha and T10, control (untreated check).
Table I.- Plant infestation by S. litura on cauliflower after different time intervals at first application of different treatments.
Treatments |
%age plant infestation after application for |
||
3 days |
5 days |
7 days |
|
T1 |
14.40±0.74 b |
11.60±0.75 b |
9.20±0.49 b |
T2 |
12.00±0.63 bcde |
9.60±0.40 bcd |
6.40±0.40 bc |
T3 |
13.60±0.75 bc |
10.80±0.80 bc |
8.80±0.48 b |
T4 |
12.40±0.74 bcd |
10.00±0.63 bcd |
6.80±0.49 bc |
T5 |
9.60±0.98 efg |
6.80±0.48 ef |
4.40±0.40 cd |
T6 |
11.60±0.97 cde |
8.80±0.49 cde |
5.60±0.40 cd |
T7 |
10.40±0.74 def |
7.60±0.24 def |
4.80±0.48 cd |
T8 |
7.60±0.40 g |
5.20±0.49 f |
2.80±0.49 d |
T9 |
8.80±0.48 fg |
6.40±0.40 ef |
4.00±0.63 cd |
T10 |
33.60±1.16 a |
35.20±1.20 a |
38.00±1.09 a |
LSD value @ 5% |
2.7314 |
2.6613 |
2.8470 |
Mean sharing the same letters within columns are not significantly different. T1, B. thuringiensis @0.5 kg/ha; T2, B. thuringiensis @1.0 kg/ha; T3, SpltNPV @ 1.0×109 POB/ml; T4, flubendiamide 480 SC @ 75ml/ha; T5, SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @0.5 kg/ha; T6, SpltNPV @ 1.0×109 POB/ml + B. thuringiensis @1.00 kg/ha; T7, SpltNPV @ 1.0×109 POB/ml + flubendiamide480 SC @ 75ml/ha; T8, B. thuringiensis @0.5 kg/ha+ flubendiamide @ 480 SC @ 75ml/ha; T9, B. thuringiensis @1.0 kg/ha + flubendiamide @480 SC @ 75ml/ha and T10, control (untreated check).
Results
Percentage plant infestation after first spray
Significant differences regarding plant infestation %age due to S. litura larvae were recorded on crop plants in the field, treated with SpltNPV, Bt. and flubendiamide alone and in combinations after three, five and seven days of 1st spray application (Table I).
Minimum plant infestation was observed three days after application where B. thuringiensis and flubendiamide were applied in combination T8 (7.60±0.40%) followed by T9, T5, T7 and T6 (8.80±0.48, 9.60±0.98, 10.40±0.74 and 11.60±0.97%, respectively). The plant infestation in T2, T4, T3 and T1 treatments (12.00±0.63, 12.40±0.74, 13.60±0.75 and 14.40±0.74%, respectively) was statistically at par. Whereas, maximum plant infestation was recorded in T10 (33.60±1.16 %) (Table I).
Five days after application, minimum plant infestation was observed where B. thuringiensis and flubendiamide were applied in combination T8 (5.20±0.49%) followed by T9, T5, T7, and T6 (i.e. 6.40±0.40, 6.80±0.48, 7.60±0.24 and 8.80±0.49%, respectively). Whereas, T2, T4, and T1 gave plant infestation 9.60±0.40, 10.00±0.63, 10.80±0.80 and 11.60±0.75%, respectively, and statistically at par with each other. While maximum plant infestation was recorded in T10 (control) i.e. 35.20±1.20. The similar trend was also observed seven days after application (Table I).
Table II.- Percent plant infestation by S. litura on cauliflower after different time intervals at second application of different treatments.
Treatments |
%age plant infestation after application for |
||
3 days |
5 days |
7 days |
|
T1 |
16.40±0.74 b |
13.20±0.80 b |
9.00±0.80 b |
T2 |
13.60±0.83 bcd |
10.80±0.48 bcd |
5.80±0.49 cd |
T3 |
16.00±0.63 b |
12.00±0.63 bc |
8.20±0.63 bc |
T4 |
14.40±0.97 bc |
11.20±0.49 bcd |
6.20±0.48 bcd |
T5 |
11.20±0.63 cde |
7.20±0.40 ef |
3.80±0.40 de |
T6 |
13.20±0.48 bcd |
9.60±0.74 cde |
5.40±0.48 cd |
T7 |
11.60±0.78 cde |
8.40±0.40 def |
4.20±0.40 de |
T8 |
8.40±0.40 e |
5.60±0.40 f |
2.20±0.40 e |
T9 |
10.00±0.63 de |
7.20±0.48 ef |
3.80±0.40 de |
T10 |
39.20±1.02 a |
41.60±1.17 a |
43.40±1.26 a |
LSD value @ 5% |
3.6618 |
3.1656 |
2.8752 |
Mean sharing the same letters within columns are not significantly different. For details of treatments, see Table I.
Percentage plant infestation after second spray
After second application, a similar pattern of plant infestation %age was recorded in all treatments. Lowest plant infestation was recorded in the plot treated with T8 (B. thuringiensis @0.5 kg/ha+ flubendiamide 480SC @75ml/ha) with plant infestation of 8.40±0.40, 5.60±0.40 and 2.20±0.40% at three, five and seven days after application, respectively. Whereas, combination treatments i.e. T9, T5, T7 and T6 also gave significant results as applied alone (10.00±0.63, 7.20±0.48 and 3.80±0.40%); (11.20±0.63, 7.20±0.40 and 3.80±0.40%); (11.60±0.78, 8.40±0.40 and 4.20±0.40 %) and (13.20±0.48, 9.60±0.74 and 5.40±0.48 %) at three, five and seven days after application, respectively. While maximum plant infestation was recorded in T10 (control) i.e. 39.20±1.02, 41.60±1.17 and 43.40±1.26 % at three, five and seven days after application, respectively (Table II).
Effect on population fluctuation of natural enemies
The results regarding the effect of different treatments on population fluctuation of natural enemies of S. litura revealed that NPV was proved toxic against all the natural enemies applied alone as well as in combination. B. thuringiensis has insecticidal activity reduced the population of all the natural enemies applied alone as well as in combination, especially with flubendiamide, but less toxic than insecticide (flubendiamide). Flubendiamide proved more toxic to natural enemies as compared with NPV and B. thuringiensis.
Although all the treatments reduced the population of natural enemies, including C. carnea, ladybird beetle and predatory bugs, but their effects were different on these natural enemies. Lady bird beetle and C. carnea were comparatively less susceptible to toxic action of treatments while predatory bugs were comparatively more susceptible to mortal action due to their delicate body. Among all the three observations recorded for each natural enemy, the maximum population of C. carnea (1.52 individuals/10 plants) ladybird beetle (1.68 individuals/10 plants) and predatory bugs (1.28 individuals/10 plants) was recorded in T3 (NPV) except control treatment. Whereas, the minimum population of C. carnea (0.48 individuals/10 plants) ladybird beetle (0.56 individuals/10 plants) and predatory bugs (0.32 individuals/10 plants) was recorded in T4 (flubendiamide 480 SC) during the first observation (Fig. 1A).
In second and third observations, similar pattern was observed where NPV was found less toxic against natural enemies with maximum population density of C. carnea (1.36 individuals/10 plants) ladybird beetle (1.52 individuals/10 plants) and predatory bugs (1.20 individuals/10 plants) was recorded for second observation and during the third observation maximum population density of C. carnea (1.20 individuals/10 plants ) ladybird beetle (1.44 individuals/10 plants) and predatory bugs (1.04 individuals/10 plants) was recorded respectively. While lowest population of C. carnea (0.32 individuals/10 plants) ladybird beetle (0.48 individuals/10 plants) and predatory bugs (0.24 individuals/10 plants) was recorded for second observation and during the third observation minimum population density of C. carnea (0.24 individuals/10 plants) ladybird beetle (0.40 individuals/10 plants) and predatory bugs (0.16 individuals/10 plants) was recorded, respectively (Fig. 1B, C).
Table III.- Mean %age mortality of S. litura on cauliflower after different time intervals at first application of different treatments.
Treatments |
%age mortality after application for |
||
3 days |
5 days |
7 days |
|
T1 |
55.91±1.63 f |
68.34±1.35 h |
75.89±1.25 f |
T2 |
65.92±1.79 cde |
73.22±1.65 ef |
83.28±1.42 de |
T3 |
59.91±2.48 ef |
70.06±0.69 gh |
77.41±1.57 f |
T4 |
63.11±1.10 de |
72.16±1.05 fg |
81.92±1.16 e |
T5 |
72.08±1.51 abc |
80.53±1.18 bc |
88.64±1.22 b |
T6 |
66.87±1.36 cd |
75.65±1.06 de |
85.29±1.46 cd |
T7 |
70.65±1.81 bc |
78.09±1.18 cd |
87.30±1.21 bc |
T8 |
77.26±1.12 a |
85.40±0.94 a |
92.67±1.30 a |
T9 |
74.39±0.93 ab |
81.57±1.20 b |
89.65±1.24 b |
T10 |
0.00 g |
0.00 i |
0.00 g |
LSD value @ 5% |
6.3853 |
2.6749 |
2.4210 |
Mean sharing the same letters within columns are not significantly different. For details of treatments, see Table I.
Percentage mortality of S. litura on cauliflower
Significant differences regarding %age mortality of S. litura larvae were recorded on the crop plants in the field, treated with NPV, Bt. and flubendiamide alone and in combinations after 3, 5 and seven days of 1st spray application (Table III).
Three days after application, maximum mortality of larvae was recorded where B. thuringiensis and flubendiamide were applied in combination T8 (0.5 kg/ha+75ml/ha) i.e. 77.26 % followed by T9, T5, T7, T6, T2, T4 and T3 (B. thuringiensis @0.5 kg/ha) i.e. 81.57, 72.08, 70.65, 66.87, 65.92, 63.11 and 59.91%, respectively. Among them T8, T9 and T5 were statistically at par with each other as well as T6 and T2 were also statistically at par with each other. Apart from T10 (control), minimum mortality was recorded in T1 i.e. 55.91%. Similar trend was observed five days after application, mortality ranged from 68.34 to 85.40%. Maximum mortality of larvae was observed where B. thuringiensis and flubendiamide were applied in combination T8 (0.5 kg/ha+75ml/ha) i.e. 85.40%. T9 and T5 were statistically at par with each other gave larval mortality 81.57 and 80.53 %, respectively followed by T7, T6, T2, T4 and T3 i.e. 78.09, 75.65, 73.22, 72.16 and 70.06%, respectively. Apart from T10 (control) minimum mortality was recorded in T1 i.e. 68.34 %, respectively.
Whereas, at seven days after application mortality ranged from 75.89 to 92.67 %. T7 treatment gave more than 80% mortality. Maximum mortality of larvae was observed where B. thuringiensis and flubendiamide were applied in combination (0.5 kg/ha+75ml/ha) i.e. 92.67%. T9, T5 and T7 were statistically at par with each other and caused larval mortality 89.65, 88.64 and 87.30 %, respectively, followed by T6, T2 and T4 i.e. 85.29, 83.28 and 81.92%, respectively. Apart from T10 (control), minimum mortality was recorded in T1 (75.89%) and T3 (77.41%) and both treatments were statistically at par with each other.
After second spray application, similar pattern of larval mortality was recorded in all treatments. Maximum mortality was recorded in plot treated with T8 (B. thuringiensis @0.5 kg/ha+ flubendiamide 480SC @ 75ml/ha) with larval mortality of 78.65, 86.63 and 93.75% at three, five and seven days after application, respectively. Whereas, the combinations T9, T5, T7 and T6 also revealed significant results (75.82, 83.56 and 90.77%); (73.17, 82.18 and 89.96%); (71.07, 80.10 and 88.79%) and (67.35, 76.68 and 86.47%) at three, five and seven days after application, respectively. While except from control treatment, minimum mortality was recorded in T1 i.e. 58.28, 67.74 and 76.53 % at three, five and seven days after application, respectively (Table IV).
Table IV.- Mean %age mortality of S. litura on cauliflower after different time intervals at second application of different treatments.
Treatments |
%age mortality after application for |
||
3 days |
5 days |
7 days |
|
T1 |
58.28±0.91 g |
67.74±1.37 g |
76.53±1.32 f |
T2 |
64.68±0.80 de |
74.27±1.32 de |
85.16±1.79 de |
T3 |
60.81±1.23 fg |
71.50±0.75 f |
79.20±1.93 f |
T4 |
62.57±0.96 ef |
73.22±0.71 ef |
83.49±1.44 e |
T5 |
73.17±1.12 bc |
82.18±1.52 bc |
89.96±1.68 b |
T6 |
67.35±1.23 d |
76.68±1.39 d |
86.47±1.50 cd |
T7 |
71.07±1.69 c |
80.10±1.13 c |
88.79±1.58 bc |
T8 |
78.65±1.04 a |
86.63±0.95 a |
93.75±1.32 a |
T9 |
75.82±0.85 ab |
83.56±1.49 b |
90.77±1.27 b |
T10 |
0.00 h |
0.00 h |
0.00 g |
LSD value @ 5% |
3.6851 |
2.7529 |
2.9061 |
Mean sharing the same letters within columns are not significantly different. For details of treatments, see Table I.
Discussion
Pakistan has a diversity of weather conditions which enable farmers to grow cauliflower throughout the year, but different insect pests caused 20 to 40 % yield losses annually (FAOSTAT, 2013). Among different insect pests, S. litura is the most serious pest which caused 31% to 100% yield loss (Lingappa et al., 2004). To overcome this pest, farmers totally relay on insecticides in Pakistan (Basit et al., 2013). Keeping in view the adverse effects of pesticides on human health, environment and beneficial insects (Khan et al., 2017; Arshad et al., 2015, 2017), the present study was designed to minimize the bad effects on human health and save our environment and conserve beneficial insects by using biopesticide and microbes. Now the world is also following this trend to control the insect pests (Crickmore et al., 2014; Khan et al., 2016; Iqbal et al., 2016; Ilyas et al., 2017).
In the current study flubendiamide has been proved very effective against this pest due to its novel mode of action and selective activity. Previous studies (Tohnishi et al., 2005; Shaurub et al., 2014; Nasution et al., 2015) have also reported that flubendiamide significantly control a broad range of lepidopterous pests, and relatively safer for predators, parasites and pollinators and environment.
The use of Bt insecticides is another safe option to control this pest because it effectively control the lepidopterous larvae, its action is fast, easy to produce at low cost, long shelf life, safer for the environment and beneficial insects and can be applied with novel pesticides in combination (Marvier et al., 2007; Kumar et al., 2008; Birch et al., 2011). In the current study B. thuringiensis in combination with other microbes significantly control this pest. Previous studies (Hokkanen and Hajek, 2003; Lacey and Merritt, 2003; Wu et al., 2005; Romeis et al., 2006; Marvier et al., 2007; Kumar et al., 2008; Birch et al., 2011; Fuentes and Jackson, 2012) are also supported our results, they reported that B. thuringiensis is a safe option and effectively control this pest by applying alone and in combination with different safer bio-pesticides.
Among entomo-pathogen viruses, SpltNPV is very important microbe, in this study SpltNPV gave hopeful results against this pest but in combination its efficacy was improved significantly. The result of current study supported by Sutanto et al. (2014), they found that SpltNPV effectively controls the larval as well as pupal stage of this pest and also controls the adult emergence.
In the current study, the results regarding plant infestation %age, population density of natural enemies and %age mortality of S. litura larvae revealed that Bt gave significant results in combination with flubendiamide and SpltNPV rather than applied alone gave significant results when applied in combination rather than alone. The current finding were parallel to the findings of previous studies (Reddy and Manjunatha, 2000; Nathan and Kalaivani, 2006; Kandalkar and Men, 2006; Singh et al., 2007, 2009; Khanna et al., 2009; Kalantari et al., 2014) they reported that Bt gave significantly higher results when applied in combination with insecticides and SpltNPV rather than alone.
Rajguru and Sharma (2014) evaluated the effectiveness of B. thuringiensis alone and in combination with water based extracts of eight plant species against S. litura larvae observed 93.33 % mortality of larvae when Bt. applied in combination with plant extract of Datura stramonium four days after application. Kalantari et al. (2014) reported synergistic action by combining Bt at lower concentration and SpltNPV at higher concentration. In conclusion, the tested chemicals could be helpful in the management of S. litura, however, further trials should be conducted in different agro-ecological zones.
Statement of conflict of interest
Authors have declared no conflict of interest
References
Abbas, N., Shad, S.A. and Razaq, M., 2012. Fitness cost, cross resistance and realized heritability of resistance to imidacloprid in Spodoptera litura (Lepidoptera: Noctuidae). Pestic. Biochem. Physiol., 103: 181-188. https://doi.org/10.1016/j.pestbp.2012.05.001
Arshad, M., Khan, H.A.A., Rehman, M.A. and Saeed, N.A., 2015. Incidence of insect predators and parasitoids on transgenic Bt cotton in comparison to non-Bt cotton varieties. Pakistan J. Zool., 47: 823-829.
Arshad, M., Khan, H.A.A., Hafeez, F., Sherazi, R. and Iqbal, N., 2017. Predatory potential of Coccinella septempunctata L. against four aphid species. Pakistan J. Zool., 49: 623-627. https://doi.org/10.17582/journal.pjz/2017.49.2.623.627
Basit, M., Saeed, S., Saleem, M.A. and Denholm Shah, M., 2013. Detection of resistance, cross resistance and stability of resistance to new chemistry insecticides in Helicoverpa armigera. J. econ. Ent., 106: 1414-1422.
Baskar, K., Sasikumar, S., Muthu, C., Kingsley, S. and Ignacimuthu, S., 2011. Bioefficacy of Aristolochia agala Cham against Spodoptera litura Fab. (Lepidoptera: Noctuidae). Saudi J. biol. Sci., 18: 23-27. https://doi.org/10.1016/j.sjbs.2010.09.004
Birch, A.N.E., Begg, G.S. and Squire, G.R., 2011. How agro-ecological research helps toaddress food security issues under new IPM and pesticide reduction policies forglobal crop production systems. J. exp. Bot., 62: 3251-3261. https://doi.org/10.1093/jxb/err064
Brousseau, C., Charpentier, G. and Belloncik, S., 1998. Effects of Bacillus thuringiensis and Destruxins (Metarhizium anisopliae Mycotoxins) combinations on spruce budworm (Lepidoptera: Tortricidae). J. Inverteb. Pathol., 72: 262-268. https://doi.org/10.1006/jipa.1998.4780
Carasi, R.C, Telan, I.F. and Pera, B.V., 2014. Biology of common cutworm (Spodoptera litura) on mulberry. Int. J. Scient. Res. Publ., 4: 1-8.
Carlton, B.C. and Gonzalez, J.M., 1986. Biocontrol of insects-Bacillus thuringiensis. In: Proceedings of the Beltsville Symposia in Agricultural Research: Biotechnology for Solving Agricultural Problems (eds. P.C. Augustine, H.D. Danforth and M.R. Bakst). Martinus Nijhoff, Boston. pp. 253-272. https://doi.org/10.1007/978-94-009-4396-4_19
Crickmore, N., Baum, J., Bravo, A., Lereclus, D., Narva, K., Sampson, K., Schnepf, E., Sun, M. and Zeigler, D.R., 2014. Bacillus thuringiensis toxin nomenclature. Available at: http://www.btnomenclature.info/ (accessed on 21 May, 2018).
FAOSTAT, 2013. Food and Agriculture Organization of United Nations. Available at: http://faostat3.fao.org/download/Q/QC/E (accessed on 21 May, 2018).
Fuentes, J.L. and Jackson, T.A., 2012. Bacterial entomopathogens. In: Insect pathology (eds. F.E. Vega and H.K. Kaya), second ed. Academic Press, San Diego, pp. 265-349. https://doi.org/10.1016/B978-0-12-384984-7.00008-7
Hokkanen, H.M.T. and Hajek, A.E. (eds.), 2003. Environmental impacts of microbial insecticides: Need and methods for risk assessment. Kluwer Academic Publishers, Dordrecht, The Netherlands, pp. 269. https://doi.org/10.1007/978-94-017-1441-9
Ignacimuthu, S. Packiam, S.M., Pavunraj, M. and Selvarani, N., 2006. Antifeedant activity of Phaeranthus indicus (L.) against Spodoptera litura (Fab.). Entomon, 31: 41-44.
Ilyas, A., Khan, H.A.A. and Qadir, A., 2017. Effect of leaf extracts of some indigenous plants on settling and oviposition responses of peach fruit fly, Bactrocera zonata (Diptera: Tephritidae). Pakistan J. Zool., 49: 1547-1553. https://doi.org/10.17582/journal.pjz/2017.49.5.1547.1553
Inglis, G.D., Goettel, M.S., Butt, T.M. and Hermann, S., 2010. Use of hyphomycetous fungi for managing insect pests. In: Fungi as biocontrol agents: Progress, problems and potential (ed. T.M. Butt). CABI Publishers, Wallingford, Oxon, GBR, pp. 23.
Iqbal, N., Evans, T.A., Saeed, S. and Khan, H.A.A., 2016. Evaluation of fipronil baits against Microtermes mycophagus (Isoptera: Termitidae). Canadian Entomol., 148: 343-352. https://doi.org/10.4039/tce.2015.56
Kalantari, M., Marzban, R., Imani, S. and Askari, H., 2014. Effects of Bacillus thuringiensis isolates and single nucleo-polyhedrosis virus in combination and alone on Helicoverpa armigera. Arch. Phytopathol. Pl. Prot., 47: 42-50. https://doi.org/10.1080/03235408.2013.802460
Kandalkar, H.G. and Men, U.B., 2006. Efficacy of Bacillus thuringiensis var. kurstaki against Sorghum Stem borer, Chilo partellus (Swinhoe). J. biol. Contr., 20: 101-104.
Khan, H.A.A. and Akram, W., 2017. Cyromazine resistance in a field strain of house flies, Musca domestica L.: Resistance risk assessment and bio-chemical mechanism. Chemosphere, 167: 308-313. https://doi.org/10.1016/j.chemosphere.2016.10.018
Khan, H.A.A., Akram, W. and Fatima, A., 2017. Resistance to pyrethroid insecticides in house flies, Musca domestica L., (Diptera: Muscidae) collected from urban areas in Punjab, Pakistan. Parasitol. Res., 116: 3381-3385. https://doi.org/10.1007/s00436-017-5659-8
Khan, H.A.A., Akram, W., Khan, T., Haider, M.S., Iqbal, N. and Zubair, M., 2016. Risk assessment, cross-resistance potential, and biochemical mechanism of resistance to emamectin benzoate in a field strain of house fly (Musca domestica Linnaeus). Chemosphere, 151: 133-137. https://doi.org/10.1016/j.chemosphere.2016.02.077
Khan, H.A.A., Akram, W., Arshad, M. and Hafeez, F., 2016. Toxicity and resistance of field collected Musca domestica (Diptera: Muscidae) against insect growth regulator insecticides. Parasitol. Res., 115: 1385-1390. https://doi.org/10.1007/s00436-015-4872-6
Khan, T., Shahid, A.A. and Khan, H.A.A., 2016. Could biorational insecticides be used in the management of aflatoxigenic Aspergillus parasiticus and its insect vectors in stored wheat? PeerJ, 4: e1665 https://doi.org/10.7717/peerj.1665.
Khanna, V., Cheema, H.K. and Taggar, G.K., 2009. Evaluation of some microbial and botanical biopesticides against Helicoverpa armigera in chickpea (Cicer arietinum). Ind. J. agric. Sci., 79: 195-198.
Kumar, S., Chandra, A. and Pandey, K.C., 2008. Bacillus thuringiensis (Bt) transgenic crop: An environment friendly insect-pest management strategy. J. environ. Biol., 29: 641–653.
Lacey, L.A. and Merritt, R.W., 2003. The safety of bacterial microbial agents used forblack fly and mosquito control in aquatic environments. In: Environmental impacts of microbial insecticides: Need and methods for risk assessment (eds. H.M.T. Hokkanen and A.E. Hajek). Kluwer Academic Publishers, Dordrecht, The Netherlands, pp. 151-168. https://doi.org/10.1007/978-94-017-1441-9_8
Lingappa, S., Basavanagoud, K., Kulkarni, K.A., Patil, R.S. and Kambrekar, D.N., 2004. Threat to vegetable production by Spodoptera litura and its management strategies. In: Fruit and vegetable diseases (ed. K.G. Mukerji). Springer, The Netherlands, pp. 357-396. https://doi.org/10.1007/0-306-48575-3_10
Marvier, M., Mc Creedy, C., Regetz, J. and Kareiva, P., 2007. A meta-analysis of effects of Bt cotton and maize on nontarget invert. Science, 316: 1475-1477. https://doi.org/10.1126/science.1139208
Nasution, D.E.A., Miranti, M. and Melanie, M., 2015. Biological Test of Formulation of Subculture Spodoptera litura Nucleo-polyhedrosis virus (SpltNPV) on Mortality of Spodoptera litura larvae infested to cabbage (Brassica oleracea Var. capitata Linn.) plantation. In: 3rd International Conference on Biological Sciences (ICBS-2013). KnowledgeE Publishing Services, pp. 646-648. https://doi.org/10.18502/kls.v2i1.237
Nathan, S.S. and Kalaivani, K., 2006. Combined effects of azadirachtin and nucleopolyhedrovirus (SpltNPV) on Spodoptera litura Fabricius (Lepidoptera: Noctuidae) larvae. Biol. Contr., 39: 96-104. https://doi.org/10.1016/j.biocontrol.2006.06.013
Nguyen, T.H.N., Borgemeister, C., Poehling, H.M. and Zimmermann, G., 2007. Laboratory investigations on the potential of entomopathogenic fungi for biocontrol of Helicoverpa armigera (Lepidoptera: Noctuidae) larvae and pupae. Biocontr. Sci. Technol., 17: 853-864. https://doi.org/10.1080/09583150701546375
Rajguru, M. and Sharma, A.N., 2014. Comparative efficacy of plant extracts alone and in combination with Bacillus thuringiensis sub sp. Kurstaki against Spodoptera litura Fab. larvae. J. Biopest., 5: 81-86.
Reddy, G.V.P. and Manjunatha, M.M., 2000. Laboratory and field studies on the integrated pest management of Helicoverpa armigera (Hübner) in cotton, based on pheromone trap catch threshold level. J. appl. Ent., 124: 213-221. https://doi.org/10.1046/j.1439-0418.2000.00466.x
Romeis, J., Meissle, M. and Bigler, F., 2006. Transgenic crops expressing Bacillus thuringiensis toxins and biological control. Nat. Biotechnol., 24: 63-71. https://doi.org/10.1038/nbt1180
Senthil, S.N., Chung, P.G. and Murugan, K., 2005. Effect of biopesticides applied separately or together on nutritional indices of the rice leaf folder Cnaphalocrocis medinalis. Phytoparasitica, 33: 187-195. https://doi.org/10.1007/BF03029978
Shaurub, E.H., Meguid, A.A. and Aziz, N.M.A., 2014. Effect of individual and combined treatment with azadirachtin and Spodoptera littoralis Multicapsid Nucleopolyhedrovirus (SpliMNPV, Baculoviridae) on the Egyptian cotton leafworm Spodoptera littoralis (Boisduval) (Lepidoptera: Noctuidae). Ecol. Balkanica, 6: 93-100.
Singh, G., Rup, P.J. and Koul, O., 2007. Acute, sublethal and combination effects of azadirachtin and Bacillus thuringiensis toxins on Helicoverpa armigera (Lepidoptera: Noctuidae) larvae. Bull. entomol. Res., 97: 351-357. https://doi.org/10.1017/S0007485307005019
Singh, H., Singh, H.R., Yadav, R.N., Yadav, K.G. and Yadav, A., 2009. Efficacy and economics of some bio-pesticide in management of Helicoverpa armigera (HUB) on chickpea. Pestology, 33: 36-37.
Singh, I.K., Ragesh, P.R., Gant, S. and Singh, A.K., 2015. Oviposition behaviour of tobacco caterpillar, Spodoptera litura (Fabricius) (Lepidoptera: Noctuidae) on different host plants. J. Ent. Zool. Stud., 3: 40-44.
Srivastava, B.K. and Joshi, H.C., 1965. Occurrence of resistance to BHC in Prodenialitura Fab. (Lepidoptera: Noctuidae). Ind. J. Ent., 27: 102-104.
Sutanto, K.D., Salamouny, S.E. and Dawood, A.S., 2014. Affectivity of Spodoptera littoralis nucleopolyhedro virus (SpliNPV) against first and second instar larvae of the cotton leafworm, Spodoptera littoralis (Boisd.). Afri. J. Microbiol. Res., 8: 337-340. https://doi.org/10.5897/AJMR2013.5352
Tohnishi, M., Nakao, H., Furuya, T., Seo, A., Kodama, H., Tsubata, K., Fujioka, S., Kodama, H., Hirooka, T. and Nishimatsu, T., 2005. Flubendiamide, a novel insecticide highly active against lepidopterous insect pests. J. Pestic. Sci., 30: 354-360. https://doi.org/10.1584/jpestics.30.354
Wu, K., Mu, W., Liang, G. and Guo, Y., 2005. Regional reversion of insecticide resistance in Helicoverpa armigera (Lepidoptera: Noctuidae) is associated with the use of Bt cotton in northern China. Pest Manage. Sci., 61: 491-498. https://doi.org/10.1002/ps.999
Yasoob, H., Khan, H.A.A. and Zhang, Y., 2017. Toxicity and sublethal effects of cantharidin on Musca domestica (Diptera: Culicidae). J. econ. Ent., 110: 2539-2544.
To share on other social networks, click on any share button. What are these?