Evaluation of Insecticidal Potentials of Five Plant Extracts against the Stored Grain Pest, Callosobruchus maculatus (Coleoptera: Bruchidae)

Simple Summary

Conventional pesticides are synthetic chemicals that are toxic, have hazardous effects on living organisms and may be carcinogenic. Pests can be controlled in an alternative way using less hazardous and more ecofriendly methods, such as using bio-pesticides. Plants based pesticides are chemicals isolated from various plants which could be used to control pests in a non-toxic mechanism. Several plants have certain bioactive compounds which could be used as alternatives to hazardous synthetic pesticides for pest control. Some beetles could damage stored grains and thus causes huge economic losses. For example, Callosbruchus maculatus is a stored grain pest which causes more than 90% damage to sored grains in a few months. Here, in this work, the insecticidal potentials of six plants, including Melia azedarach, Nicotiana rustica, Azadirachta indica, Nicotiana tabacum and Thuja orientalis, were investigated against C. maculatus. Crude extracts of these plants at different concentration were checked against C. maculatus and mortality was observed. Maximum mortality was caused by N. tabacum and N. rustica (100%) followed by A. indica (82%), whereas minimum mortality was observed in T. orientalis (64%) at 2.5%. The results of this study revealed that the extracts of these plants could be used for the control of stored grain pests.

Abstract

Plant based insecticides are considered among the most economic and ecofriendly chemicals for the protection of plants and stored grains. The cowpea weevil (Callosbruchus maculatus) causes more than 90% damage to sored grains in three to six months. The current study investigates insecticidal potentials of five selected botanicals: Melia azedarach, Nicotiana rustica, Azadirachta indica, Nicotiana tabacum and Thuja orientalis. They are explored at six different concentrations (0.5, 1.0, 1.5, 2.0, 2.5 and 3.0%) against C. maculatus and compared to effects of distilled water which is used as a control. Toxicities of 3%(V/V) extracts of N. tabacum, N. rustica, A. indica and T. orientalis against C. maculatus were 100%, 86.11%, 80.56% and 72.22%, respectively. Maximum mortality was caused by N. tabacum and N. rustica (100%), followed by A. indica (82%), whereas minimum mortality was observed in T. orientalis (64%) at 2.5%. Several phytochemicals, alkaloids, saponins, diterphenes, phytosterol, flavonoids and phenols were identified in N. tabacum and N. rustica, while few were present in A. indica. Phytosterol was present in greatest abundance. Saponins were only detected in aqueous extracts of N. rustica and N. tabacum. Taken together, these results indicate the utility of N. tabacum, N. rustica and A. indica as potential botanicals to control pest beetle and cowpea weevil.

1. Introduction

The demand for food increases with an ever-growing population. Thus, it is necessary to protect crops and stored grains from pests. The multivoltine pest, cowpea weevil Callosobruchus maculatus Fab. (Coleoptera: Bruchidae), causes significant damage to stored pulses [1]. It has been reported that C. maculatus alone can cause as much as 90% damage during the three to six months of storage [2]. Due to their potencies to cause lethality in most life stages of a range of pests, synthetic pesticides are frequently used to protect both crop plants and stored grains [3]. Synthetic pesticides can adversely affect non-target organisms, including humans, accumulate in the environment, pollute soil and ground water. Some of the synthetic pesticides are also carcinogenic [4]. The overuse of synthetic pesticides for insect control poses risks to wildlife and even humans [5]. Toxic potency of synthetic pesticides and their potential effects have stirred interest from the public and regulatory agencies in alternative options for pest management [6].

Until the relatively recent development of synthetic pesticides and their widespread application since the 1940s, phytochemicals have long been successfully used to manage pests in crops [7]. Extracts of plants and other secondary metabolites of plants, microorganisms and enzymes are becoming increasingly popular as alternatives to synthetic pesticides [8]. Bio-insecticides can be very effective, selective and have little potential for developing resistance to target pests, as well as having minimal effects on non-target organisms [9].

Several plant extracts have been used to control various stored insect pests. Essential oils of some aromatic plants have been recognized to have cytotoxic, antioxidant, antifungal, insecticidal and antibacterial properties [10]. The aqueous extract of neem kernel has been used to protect crops from infestation with pests [11,12]. The species of the deciduous tree in the mahogany family, Meliaceae, commonly known as the chinaberry tree, pride of India, bead-tree, Cape lilac, syringa berry tree, Persian lilac, Indian lilac and white cedar (Melia azedarach) have insecticidal properties against several pest species [13]. The tobacco plants Nicotiana. tabacum and Nicotiana. rustica are also able to control several insect pests. Nicotine present in N. tabacum and N. rustica cause uncontrolled nerve firing and masking acetylcholine in insects, which results in death [13]. The present study was conducted to evaluate insecticidal potencies of extracts of five plants against C. maculatus. The toxic potencies of the five botanicals, M. azedarach, N. rustica, A. indica, N. tabacum and T. orientalis, against the cowpea weevil, C. maculatus, are investigated.

2. Materials and Methods

2.1. Collection of Insects

Cowpea weevil, Callosobruchus maculatus, were collected from various regions of the Swabi and Haripur districts of the Khyber Pakhtunkhwa province in Pakistan. C. maculatus were taken to the entomological laboratory and identified according to previous reports [14]. Adults of C. maculatus were chosen to initiate the culture at the entomological laboratory under laboratory conditions of 27.5 °C, 60 ± 5% RH and a 12L:12D photoperiod on the entire mung bean (Vigna radiate L.), which is known to be an ideal host in plastic jars (10 × 12 cm) enclosed in muslin fabric [15].

2.2. Plants Collection

Leaves and fruits of the specified selected plants were collected from various areas in the Swabi and Haripur districts of the Khyber Pakthunkhwa in Pakistan, according to previously described procedures [16] (

Table 1. List of plant species and plant parts tested against C. maculatus during 2021.

Sr. No.	Common Name	Botanical Name	Family	Part Used
1.	White Patta	Nicotiana rustica	Solanaceae	leaf
2.	Virginia tobacco	Nicotiana tabacum	Solanaceae	leaf
3.	Chinese arborvitae	Thuja orientalis	Cupressaceae	Fruit
4.	Neem	Azadirachta indica	Meliaceae	Seed
5.	Bakion	Melia azadarech	Meliaceae	Fruit

).

2.3. Phytochemical Screening

Extracts of selected plants were screened for the presence of various bio-active compounds, such as alkaloids, phenols, phytosterol, terpenes and flavonoids. The detection of these compounds was carried out using standard tests, as reported in literature.

2.3.1. Maceration

Coarsely powdered plant material was extracted in a container of methanol and ethyl acetate and hexane) and agitated for a defined period.

2.3.2. Detection of Alkaloids, Phenols, Phytosterol, Terpenes and Flavonoids in Plant Extract

A few drops of iodine and two to three drops of potassium iodide were dissolved individually in diluted hydrochloric acid (1.5%). One milliliter of this reagent was added to plant extracts and stirred for five minutes. Dark reddish precipitates were observed in the samples, which indicates the presence of alkaloids in plants extracts [17,18]. For the screening of phenol, three to four drops of ferric chloride solution were added to plant aqueous extracts. The formation of a bluish black color indicates the presence of phenols in the extract [18]. Similarly, for the detection of phytosterol, extracts of the selected plants were cured with chloroform and then filtered. Few drops of concentrated sulfuric acid were added into the filtered extract and allowed to be undisturbed for a few minutes. The formation of a golden yellow color indicates the presence of phytosterol [19]. For the determination of diterpenes in the selected plants extracts, three to four drops of copper acetate solution were added into the aqueous extracts of the selected plants. The formation of emerald green color indicates the presence of diterpenes [20]. Flavonoids were detected in plants extracts by adding two to three drops of lead acetate solutions to the plant aqueous extracts. A bright yellow color appeared, which indicates the presence of flavonoids in the sample. The color disappeared when few drops of dilute acid was added [21].

2.4. Residual Toxicity

Residual toxicity of extracts was determined according to previously described methods (22). In this study, five plant extracts and six different concentrations (

Table 2. Plant extract and their concentrations used against C. maculatus during 2021.

Sr. No.	Common Name	Botanical Name	Concentration Used
1.	White Patta	Nicotiana rustica	0.5, 1, 1.5, 2, 2.5 and 3%
2.	Virginia tobacco	Nicotiana tabacum	0.5, 1, 1.5, 2, 2.5 and 3%
3.	Chinese arborvitae	Thuja orientalis	0.5, 1, 1.5, 2, 2.5 and 3%
4.	Neem	Azadirachta indica	0.5, 1, 1.5, 2, 2.5 and 3%
5.	Bakion	Melia azadarech	0.5, 1, 1.5, 2, 2.5 and 3%

) were tested, following the CRD design with (6 × 5) factorial arrangement with four replicates. Sterilized test sample of mung bean (20 g) were treated with plant extracts (Table 2) separately, then air-dried for 30 min. Treated legumes were then put in plastic petri dishes (12 cm diam.). Five pairs of newly emerged adults were released in each petri dish and covered with muslin cloths to prevent the escapes of beetles from the testing arena. Mortality of C. maculatus in each petri dish was assessed after 24, 48, 72, 168 and 336 h of exposure. Dead beetles from each petri dish were removed and counted. Corrected mortality (23) for each treatment was calculated as per the following formula (Equation (1)).

$$Corrected \% Mortality=\frac{\% mortality in treatment-\% mortality in control}{100-\% mortality in control}\times 100$$

(1)

2.5. Topical Toxicity

Topical toxicity of the plant extracts (Table 2) was also investigated against C. maculatus adult beetles. The same experimental design and treatment in Section 2.4 were applied here. The concentrations of plant extracts (Table 2) were applied through pipet onto the thoracic segment of C. maculates, then wrapped in aluminum foil and stored in the refrigerator for five minutes before being treated. All treated C. maculatus adults were put in plastic petri plates with the help of a camel hairbrush. After exposure for 24, 48, 72, 168 and 336 h, the number of dead beetles was counted and the percentage mortality (%) for each concentration was calculated.

2.6. Statistical Analysis

While normality was checked using the Shapiro–Wilks test, the assumption of homogeneity of variance was evaluated using Levene’s test. The Tukey HSD analysis was applied at 5% probability of Type I error (α) to separate the means of the obtained data from recent research using Analysis of Variance (ANOVA). Statistical analyses were carried out using STATISTIX 8.1 (24). The mortality percentages were corrected using Abbott’s formula. Thereafter, the Log-Probit model analysis was applied to percentage mortality of the adult C. maculatus to determine the 50% and 90% lethal concentrations (LC50/LC90) (25). The Analysis of Variance and the Probit analyses were done using the Statistical Package for the Social Sciences (SPSS) version 20.

3. Results

Several phytochemicals, including alkaloids, saponins, di-terphenes, phyto-sterol, flavonoids and phenols, were identified in N. tabacum and N. rustica, while few were present in A. indica. Phytosterol was present in greatest abundance. Saponins were detected only in aqueous extracts of N. rustica and N. tabacum (

Table 3. Composition of phytochemicals in aqueous extracts of five selected plants species.

	Phytochemical Constituents of Five Plant Species
Plant Species	Alkaloids	Flavonoids	Saponins	Di-Terpenes	Phyto-Sterol	Phenols
T. orientalis	Low	low	low	low	Low	low
M. azedarach	low	low	low	low	moderate	moderate
N. rustica	low	low	not present	low	Low	low
A. indica	High	high	moderate	moderate	High	high
N. tabacum	moderate	moderate	moderate	high	moderate	high

).

The insecticidal activity of plant aqueous extracts was tested against C. maculatus to six concentrations (0.5, 1.0, 1.5, 2.0, 2.5, and 3.0%). Data pertaining to insecticidal activity of the selected plant extracts both in residual (Figure 1 and

Table 4. Mortality of C. maculatus exposed to aqueous extracts for 24, 48, 72, 168 and 336 h.

Time Hours	Plant Species	N*	LC50 95% LC	X2	P	Slope + SE
24	A. indica	240	38.44 (15.77–740.47)	0.85	0.93	0.96 ± 0.26
	N. rustica	240	37.19 (16.02–495.66)	1.59	0.80	1.07 ± 0.28
	M. azedarach	240	29.73 (16.01–359.42)	2.28	0.68	1.44 ± 0.37
	N. tabacum	240	24.73 (18.12–1308.62)	0.69	0.95	1.05 ± 0.29
	T. orientalis	240	54.85 (18.42–1892.92)	1.37	0.84	1.50 ± 0.53
48	A. indica	240	32.24 (12.10–366.33)	1.73	0.78	2.36 ± 0.75
	N. rustica	240	30.27 (14.92–224.42)	0.82	0.58	0.63 ± 0.37
	M. azedarach	240	24.20 (9.91–335.57)	1.62	0.80	3.43 ± 1.40
	N. tabacum	240	20.75 (23.91–6190.66)	0.99	0.91	1.22 ± 0.37
	T. orientalis	240	35.50 (13.60–7305.06)	1.76	0.78	2.13 ± 0.79
72	A. indica	240	28.36 (13.71–217.70)	1.17	0.88	1.06 ± 0.26
	N. rustica	240	24.39 (12.49–148.61)	0.40	0.98	1.06 ± 0.26
	M. azedarach	240	29.57 (14.34–220.30)	0.49	0.97	1.16 ± 0.28
	N. tabacum	240	17.53 (10.27–62.95)	1.39	0.84	1.12 ± 0.24
	T. orientalis	240	29.01 (14.35–194.43)	2.37	0.66	1.22 ± 0.29
168	A. indica	240	6.32 (4.89–9.95)	1.75	0.78	1.17 ± 0.21
	N. rustica	240	5.44 (4.23–8.48)	3.06	0.54	1.06 ± 0.20
	M. azedarach	240	9.15 (5.40–101.82)	7.04	0.13	1.18 ± 0.22
	N. tabacum	240	4.75 (3.74–7.01)	3.16	0.53	1.03 ± 0.20
	T. orientalis	240	8.39 (6.20–14.91)	1.76	0.77	1.23 ± 0.22
336	A. indica	240	1.86 (1.43–2.24)	4.94	0.29	1.40 ± 0.20
	N. rustica	240	1.34 (0.93–1.69)	4.83	0.30	1.39 ± 0.20
	M. azedarach	240	1.72 (1.21–2.15)	6.58	0.16	1.19 ± 0.20
	N. tabacum	240	0.92 (0.04–1.61)	17.36	0.00	1.79 ± 0.23
	T. orientalis	240	2.55 (2.10–3.02)	3.94	0.41	1.41 ± 0.20

N* = number of insects used; LC Lethal concentration are indicated with 95% confidence limit (CL,). LC50 of plant extract g/mL.

) and direct (Figure 2 and

Table 5. Toxicological effect (Direct) of plant extracts against C. maculatus after 24, 48, 72, 168 and 336 h’ exposure period.

Time	Plant Species	N*	LC-50 95% LC	X2	P	Slope + SE
24	A. indica	240	44.55 (17.88–987.72)	1.40	0.57	0.55 ± 0.16
	N. rustica	240	36.33 (15.83–462.57)	0.23	0.99	0.47 ± 0.12
	M. azedarach	240	36.33 ((15.83–462.57)	0.23	0.99	0.47 ± 0.12
	N. tabacum	240	28.84 (13.47–278.34)	0.05	1.00	0.42 ± 0.11
	T. orientalis	240	51.87(19.25–1985.44)	2.92	0.84	0.54 ± 0.15
48	A. indica	240	29.78 (13.83–287.89)	0.89	0.99	0.40 ± 0.11
	N. rustica	240	28.59 (12.92–362.31)	0.04	1.00	0.38 ± 0.10
	M. azedarach	240	32.31 (14.06–474.14)	0.32	0.98	0.39 ± 0.10
	N. tabacum	240	16.23 (9.38–65.90)	0.31	0.98	0.42 ± 0.10
	T. orientalis	240	40.86 (16.18–921.48)	0.825	0.92	0.39 ± 0.11
72	A. indica	240	13.08 (6.60–742.10)	1.43	0.83	0.92 ± 0.21
	N. rustica	240	10.21 (5.71–176.58)	2.43	0.65	0.94 ± 0.21
	M. azedarach	240	15.13 (7.23–1536.29)	0.91	0.92	0.93 ± 0.22
	N. tabacum	240	7.73 (4.92–37.88)	2.37	0.66	1.05 ± 0.21
	T. orientalis	240	23.97 (11.25–287.51)	2.00	0.73	0.68 ± 0.23
168	A. indica	240	2.73 (1.92–3.68)	2.12	0.71	1.32 ± 0.32
	N. rustica	240	1.94 (1.17–2.57)	7.90	0.09	1.35 ± 0.32
	M. azedarach	240	3.24 2.03–5.76)	4.33	0.36	0.94 ± 0.31
	N. tabacum	240	1.66 (1.06–2.16)	11.09	0.02	1.64 ± 0.32
	T. orientalis	240	4.25 (2.93–9.40)	3.84	0.42	1.00 ± 0.32
336	A. indica	240	0.31 (0.00–0.082)	7.88	0.09	1.29 ± 0.25
	N. rustica	240	0.32 (0.00–0.89)	12.85	0.01	1.55 ± 0.28
	M. azedarach	240	0.20 (0.00–0.54)	1.46	0.83	0.79 ± 0.22
	N. tabacum	240	0.19 (0.001–0.56)	8.82	0.06	1.43 ± 0.31
	T. orientalis	240	0.55 (20.01–9.40)	3.89	0.42	0.61 ± 0.20

N*= number of insects used; LC Lethal concentration are indicated with 95% confidence limit (CL,). LC50 of plant extract gm/mL.

forms are represented.

Among the plant species extracts, the highest residual mortalities of C. maculatus was observed with N. tabacum with 6.25%, followed by N. rustica with 5.83% and A. indica with 3.33%. Lowest mortalities were observed with T. orientalis, i.e., 1.66%, followed by M. azedarach, i.e., 2.50% (df = 4, F = 10.48, p = 0.000), after 24 h of exposure period (Figure 1A). The LC50 values towards C. maculatus among the plant extracts were 24.73 for N. tabacum, followed by 29.73 for M. azedarach. The extract of T. orientalis with an LC50 of 54.85 was the least efficacious of the extracts (Table 4).

The exposure time was further increased to 48 h to check the effect of these selected five plants extracts on the mortality of pests. Figure 1B shows the effects of the six different concentrations of five different plant species crudely extracted after the 48-h exposure period. Crude extracts showed significant mortality on C. maculatus. Maximum mortalities of 12.91% were recorded with N. rustica, followed by N. tabacum with 11.67% and A. indica with 9.16%, while minimum mortalities to C. maculatus were recorded with T. orientalis with 3.75%, followed by M. azedarach with 7.50% (df = 4, F = 06.46, p = 0.0001). The LC50 values, based on mortality of C. maculatus, were 20.75 for N. tabacum, followed by 24.20 for M. azedarach (Table 4). T. orientalis, which exhibited values for mortality of 35.50, were the least efficacious.

Extracts of the five different tested plant species had significantly impacted the mortality of C. maculatus after the 72-h exposure period (Figure 1C). C. maculatus mortalities were higher at N. tabacum with 20.00%, followed by N. rustica with 18.00% and A. indica with 16.00%. Lower mortalities of 12.50% were seen with T. orientalis, followed by M. azedarach with 13.00% (df = 30, F = 07.11, p = 0.0001). The LC50 value for N. tabacum against C. maculatus was 17.53, followed by N. rustica with 24.39 and T. orientalis with 29.01 (Table 4).

Results represented in Figure 1D indicate significant mortality rates of the five different plant species crudely extracted for six different concentrations after 168 h of exposure to C. maculatus. The mortality rates of C. maculatus increase as the exposure time increases. C. maculatus mortalities were higher with N. tabacum with 39.00%, followed by N. rustica with 36.00% and A. indica with 32.00%. Lower mortalities of 25.00% were recorded with T. orientalis, followed by M. azedarach with 26.00% (df = 4, F = 20.30, p = 0.0000). From Table 4, it was clear that the LC50 of N. tabacum is 4.75, followed by N. rustica with 5.44 and A. indica with 6.32, whereas T. orientalis and M. azedarach have LC50 values of 8.39 and 9.15, respectively.

Finally, results presented in Figure 1E revealed significant mortality rates of five different plants species crude extracts of six different concentrations after fourteen days of exposure to C. maculatus. The highest mortalities of C. maculatus were noted with N. tabacum with 77.00%, followed by N. rustica with 56.00%. A. indica and M. azedarach exhibited the same mortalities of 56.00%, while the lowest mortalities of 49.00% were seen with T. orientalis (df = 4, F = 33.80, p = 0.0000). In case of LC50 values from Table 4, it was clear that N. tabacum revealed 0.92, followed by N. rustica with 1.34 and A. indica with 1.72, whereas T. orientalis and M. azedarach resulted in 2.55 and 1.86, respectively. The mean percent (±SE) residual mortality of C. maculatus after various time intervals is given in the supplementary file (Tables S1–S5) and the mean percent (±SE) topical mortality of C. maculatus after various time intervals is given in the supplementary file (Tables S6–S10).

Among the plant species extracts, the highest mortalities of C. maculatus were observed with N. tabacum of 15.00%, followed by N. rustica with 12.00%. The lowest mortality was observed with T. orientalis with 7.00%, followed by A. indica and M. azedarach, both with 7.00% (df = 4, F= 10.48, p = 0.00) after the 24-h exposure period (Figure 2A). In case of LC50, N. tabacum had 28.84, followed by N. rustica and M. azedarach with 36.33, were most effective. T. orientalis (51.87) was least effective against C. maculatus (Table 5).

The exposure time was further increased to 48 h to check the effect of these selected five plants extracts on the mortality of pests. Figure 2B shows the effects of six different concentration of five different plant species crudely extracted after the 48-h exposure period. Crude extracts showed significant mortality on C. maculatus. A maximum mortality of 18.00% was recorded with N. tabacum, followed by N. rustica with 17.00% and A. indica with 14.00%. A minimum mortality of 10.00% to C. maculatus was recorded with T. orientalis, followed by M. azedarach with 14.00% (df = 4, F = 06.46, p = 0.0001). From Table 5, it was clear that among the plant species N. tabacum (16.23), followed by N. rustica (28.59) and M. azedarach (32.31), gave promising results in killing 50% of the tested population of C. maculatus. T. orientalis’s (40.86) mortality showed the lowest effectiveness.

Extracts of five different tested plant species had significantly impacted the mortality of C. maculatus after the 72-h exposure period (Figure 2C). C. maculatus mortalities were higher at N. tabacum with 30.00%, followed by N. rustica with 28.00%, A. indica with 25.00% and M. azedarach with 22.00%. Lower mortalities of 18.00% were seen with T. orientalis (df = 30, F = 07.11, p = 0.0001). In case of LC50, N. tabacum (7.73), followed by N. rustica (10.21) and A. indica (13.08), were most effective, while T. orientalis (44.99) was found least effective against C. maculatus, as shown in Table 5.

Results represented in Figure 2D indicate significant mortality rates of five different plant species crudely extracted at six different concentrations after a 168-h exposure period on C. maculatus. The mortality rates of C. maculatus increases as the exposure time increases. C. maculatus mortalities were higher with N. tabacum by 60.00%, followed by N. rustica at 54.00%, A. indica at 46.00% and M. azedarach at 41.00%. A lower mortality of 36.00% was recorded with T. orientalis (df = 4, F = 20.30, p = 0.0000). In case of LC50, N. tabacum at 1.66, followed by N. rustica at 1.94 and A. indica at 2.73, were the most effective, while T. orientalis at 4.25 and M. azedarach at 3.24 were found the least effective against C. maculatus, as shown in Table 5.

Finally, results presented in Figure 2E revealed significant mortality rates of five different plants species crudely extracted at six different concentrations after fourteen days of exposure on C. maculatus. The highest mortalities of C. maculatus were noted with N. tabacum at 92.00%, followed by N. rustica at 88.00% and A. indica at 83.00%, while the lowest mortalities were seen at 63.00% with T. orientalis and 74.00% with M. azedarach (df = 4, F = 33.80, p = 0.0000). Among the plant extracts, N. tabacum at 0.19, followed by N. rustica at 0.20, were more promising in killing 50% of the tested population of C. maculatus. T. orientalis at 0.31 mortality showed the lowest effectiveness, as shown in Table 5.

4. Discussion

4.1. Mortality of C. maculatus Exposed to Each of Five Plants

Crude extracts of A. indica, N. tabacum. N. rustica, M. azedarach and T. orientalis were mixed with 20 g mung bean at the rate of 0.5%, 1%. 1.5, 2%. 2.5% and 3%, respectively. At all the concentrations tested, crude extracts of N. tabacum, N. rustica, A. indica and M. azedarach showed more residual toxicity against C. maculatus. Our findings are similar to the findings of a past study [22] suggesting that crude extracts of N. tabacum had the highest residual toxicity against Tribolium castaneum, i.e., 89% at a 3% concentration. Botanical insecticides contain a range of bioactive compounds that have potential to cause adverse effects on organisms that either consume them or are exposed to them. In particular, plants have co-evolved with insects that eat them, so they have developed defense mechanisms, including production of compounds that disrupt normal physiology and behavior of insects, thus, affecting eating, mating, mortalities and oviposition [23]. Secondary metabolites, N. tabacum and N. rustica, including alkaliods, flavoniods, saponins and di-tarphene can repel or kill insects. Alkaloids, including nicotine, act as stomach poison in insects. Tobacco leaves contain physiologically active chemicals that paralyze insects by acting on their central nervous system. When they feed on plants containing these compounds insects ultimately die [24]. It has recently been observed that when relatively large amounts of A. indica was consumed in the diet of C. maculatus, significant mortalities were observed [25]. The major mechanism of action of azadirichtin has been reported to limit the release of neurosecretory material from the corpora cardiaca, resulting in a slower turnover rate, as well as altering the prothoracicotropic hormone (PTTH) via brain neurosecretory cells [26]. The results of this study are consistent with those reported previously suggesting that pulses sprayed with crude extracts of M. azedarach were well-preserved for up to six months without evidence of infestation [27]. Results of this study revealed insecticidal potency via topical application through consumption in the diet of C. maculatus without treating any mung bean seeds. Among the plants tested, N. tabacum, followed by N. rustica, A. indica and M. azedarach, exhibited significantly maximum accumulative mortality, whereas T. orientalis caused minimum mortality. The mechanism of entrance of the active components into the target location in insects can also be attributed to variations in potencies to cause mortality of the extracts. Biocidal ingredients of extracts are thought to enter the insect through the integument [28]. Specifically, toxins have been reported to gain access to the target areas through the lipophilic and hydrophilic cuticle, where they cause a variety of effects through multiple mechanisms. The hydrophilic-hydrophobic structure of the cuticle has been reported to influence penetration of pesticides which also controls their efficacy [29]. Chemical properties of active principals and polarity influence passage of bioactive compounds, like insecticides through the cuticle. The cuticle’s outermost lipophilic phase promotes nonpolar molecular mobility. As a result, only toxins in extracts with a favorable polarity and chemical composition were able to penetrate to an internal site of toxic action, which could initiate molecular responses that result in lethality. A dose-response relationship was observed between the concentration of a given crude plant extract and the corresponding percent mortality, which is consistent with the results reported previously [30].

4.2. Mortality of Selected Plants Extracts against C. maculatus

The harmful effects of the compounds in extracts of the studied plants observed in this study might have contributed to the mortality of C. maculatus, which is in close agreement with other similar works reported in literature [31]. Even though all of the plants exhibited promise as insecticides, their toxic potencies against C. maculatus differed, most likely due to differences in phytochemical composition. Currently N. tabacum exhibited the greatest mortality of C. maculatus at concentrations of 3% [32]. This also confirms the same results that N. tabacum exhibits high mortality of pulse beetle at 3% concentration. As suggested previously, secondary metabolites contained in these plants might be responsible incapacity of adult C. maculatus [33].

4.3. Phytochemical Analysis Five Plants Extracts

Nicotiana tabacum contains relatively great concentrations of alkaloids, phenolic compounds, flavonoid, tannins, saponins, terpenoids, various proteins and carbohydrates. This result is consistent with previous reports of constituents in extracts of this plant. Nicotine, the active ingredient of N. tabacum, has been documented to have contact, stomach, and respiratory poisoning effects [33]. Saponins, alkaloids, flavonoids, tannins and cyanogenic glucosides are all found in crude extracts of A. indica. The natural phytochemicals from plants have a potential of being eco-friendly and replace synthetic pesticides for insect pests [34].