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Biocontrol efficacy of bay essential oil against housefly, Musca domestica (Diptera: Muscidae)



The synanthropic housefly, Musca domestica, augments the transmission of several detrimental diseases like cholera and avian flu. Consequently, during the last century, many physico-chemical methods including synthetic compounds have been applied for its control. But these methods have proven to be prohibitive due to their side effects and serious issues like resistance development, environmental contamination, and detrimental effects on non-target fauna. Therefore, in view of these objectives, we investigated the effects of bay essential oil (EO) against M. domestica.


The attractant/repellent assays were conducted by double choice technique. Different enzyme assays evaluating the effect of LC50 concentration of the tested essential oil on larval gut were taken into consideration. To determine the composition, the tested oil was subjected to GC-MS/MS analysis. Further, the morphological alterations caused by EO treatment to third instar larvae were observed in a Nova Nano SEM machine. Data was statistically analyzed by one-way ANOVA using Tukey’s test (p < 0.001). The LC50 and LC90 values were calculated by probit analysis.


The adulticidal bioassay revealed significant effects with LC50 concentration as 43.03 mg/dm3 against the newly emerged adult flies while in larvicidal assay mortality was dose dependent showing maximum effect at LC50 0.0629 μg/cm2. The pupicidal activity was more effective at a dose of LD50 64.09 μl/0.25 L of air which either killed the pupae or caused deformity in the emerged adults. Likewise total sugar, protein, glycogen, and lipid contents of larvae were reduced after treatment with EO when compared with the normal larvae along with some gut enzymes. The EO reduced the acetylcholinesterase activity from 0.013 U/mg protein in normal larvae to 0.0093 U/mg protein after EO treatment. The GC-MS/MS analysis of the bay EO showed the abundance of myrcene, linalool, eugenol, chavicol, and anethole along with diterpenoid, geranylgeraniol. However, the insecticidal activity of tested EO might be majorly imparted by eugenol content. The FESEM analysis showed shrinkage of integument and distortion to intersegmental regions caused by the tested compound.


The present study concludes the significant efficacy of bay EO against M. domestica which could be employed to breakdown its population below threshold levels to prevent the menace of vector-borne diseases.


The housefly, Musca domestica (Diptera: Muscidae), is a well-known pest of livestock and human health importance. It constitutes a worldwide problem wherever poor sanitation and bad hygienic conditions exist (Khan et al., 2013). Moreover, the biology and ecology of Musca domestica makes it an ideal organism to carry and disseminate human and animal pathogens, such as helminth parasites, protozoan cysts, viruses, and bacteria (Fotedar et al., 1992; Greenberg, 1973; Kobayashi et al., 1999). Recently, it has been inculpated to transmit avian flu (Wanaratana et al., 2013) also. Therefore, hitherto, a large variety of synthetic compounds such as DDT and cyromazine have been used against this vector to prevent the epidemics. However, indiscriminate use of these chemical insecticides has resulted in many serious problems like insect resistance, persistence of chemicals in the environment, and biomagnifications through trophic levels leading to detrimental effects on human beings (Tabashnik & Johnson, 1999). Therefore, researchers are continuously prospecting for active natural products of plant origin as potential alternatives to conventional insecticides.

The eco-toxicological property of plants such as lower toxicity to humans, cheap, easy cultivation and degradation along with reduced environmental impact makes them promising candidates for the management of insect pests (Kumar et al., 2011). Additionally, aromatic plants have proved effective insecticides and their essential oils (EOs) often constitute the bioactive fraction (Regnault-Roger, 1997). Plant metabolites act by either exerting their effect on octopaminergic nervous system of insect pests (El-Zayyat et al., 2017) or interfering with GABA-gated chloride channels (Khater, 2012). Further effects can be seen in behavioral modifications (attraction/repellency) and contact toxicity for different life stages of the targeted organisms. Similarly, some natural oils are complexes of many biologically active constituents including terpenes, acyclic monoterpene alcohols, monocyclic alcohols, aliphatic aldehydes, aromatic phenols, monocyclic ketones, bicyclic monoterpenic ketones, acids, and esters (Koul, 2008).

In the past few years, there is a strong impetus to develop EOs of botanical origin as potential agents for pest control strategies. Since aromatic angiosperm, Laurus nobilis L., is widely exploited for treatment of gastrointestinal disorders (Lorenzi & Matos, 2008), the aqueous extracts of this plant are also used for the treatment of many open wounds from ancient times (Nayak et al., 2006). In view of these properties, the present study aimed to determine the chemical composition of Laural nobilis essential oil and evaluate its efficiency against Musca domestica. Further, we investigated the larvicidal effect and oviposition deterrent activities posed by this oil to the different life stages of the fly.

Materials and methodology

Chemicals and reagents

The EO of the Laurus nobilis was supplied by Sigma Aldrich, USA. The oil doses were prepared freshly by dilution in acetone solvent and immediately used for tests. All other chemicals/reagents used in this study were of highest purity and molecular or analytical grade unless defined.

Rearing of housefly colony

The laboratory-reared colonies of the model organism, i.e., M. domestica, were generously provided by the Entomology Section, National Chemical Laboratory (NCL), Pune (M.S.), India, which were free from insecticides and pathogens. The culture of housefly was maintained in vitro at a temperature of 28 ± 2 °C and 60–70% relative humidity (RH) in plastic jars (35 × 15 cm), covered with cheese cloth for several generations. A cotton swab soaked in milk (10% w/v) was offered as a food to adult flies which also served as a substratum for oviposition. The eggs were transferred to another set of jars containing animal feed and water or cotton swab soaked in milk for hatching and larval development. Similarly, pupae were collected and kept in another container for adult emergence. All stages of the fly such as eggs, larvae, pupae, and adults were continuously available for the experiments.

Larvicidal and adulticidal bioassays

The larvicidal and adulticidal bioassays were carried out by following the methods of Busvine (Busvine, 1971) and Palacios et al. (2009), respectively, with few modifications. To determine the effect of EO, 10 individuals of the third instar larvae were exposed to different concentrations of EO in each test. Primarily, a range of desirable doses were tested to determine the LC50 and LC90 values. For residual film method, 1 ml each of different concentrations of EOs was applied on filter paper discs kept inside the glass petri dish of 90 mm diameter. The EO doses were applied uniformly in order to make a uniform film over the filter paper. Initially, the treated petri dishes were air dried for few minutes to allow the solvent evaporation, followed by release of larvae (n = 10) and then incubating the plates under laboratory conditions for 24 h.

In case of adulticidal assay, 10 adult flies were placed in plastic jars (1.2 dm3) containing a 7-cm-long cotton yarn suspended from the cap of the jar. Different dosages of EO ranging from 10 to 100 mg/dm3 were used for the tests. Each dose was applied after being dissolved in 10 μl of acetone then applied to a cotton yarn. In the control jar, the cotton yarn was treated with 10 μl of acetone only. The jars were then sealed tightly and kept at 28 ± 2 °C for 30 min. All tests were replicated five times with acetone solution being used as a control treatment. The mortality rate of the treated larvae and flies was calculated after 24 h of treatment by using below mentioned formula 1. Where X denotes the percentage of larvae that survived in the control test and Y represents the percentage survival of larvae in the tested doses.

$$ \mathrm{Mortality}\left(\%\right)=\left[X-Y/X\right]100 $$

The data were pooled and analyzed by standard probit analysis to obtain LC50 and LC90 values. However, the actual dose of EO present in 1 ml mixture was calculated by using the formula 2.

$$ \mathrm{Dose}/{\mathrm{cm}}^2=\mathrm{value}\kern0.3em \mathrm{present}\kern0.3em \mathrm{in}\kern0.3em 1\kern0.3em \mathrm{ml}/\mathrm{area}\kern0.3em \mathrm{of}\kern0.3em \mathrm{petridish} $$

Attractant/repellant bioassays

The attractant and repellant bioassays were carried out by using the double choice method (Campbell, 1983) where 20 newly emerged adults of mixed sexes were released in a cage (size 20 × 12 × 8 cm) with two conical flasks. One flask contained 0.1% test oil in 5 ml of milk, while the other contained acetone as a solvent and 5 ml of milk to serve as control. The conical flasks were fitted with funnel (10 cm in diameter) to avoid the escape of the flies. The assays were replicated five times, and the numbers of flies attracted towards the tested oil flask and in the control flask were counted after 24 h to determine the percentage of repellency. The results were expressed in terms of percentage (%) attraction whereas percentage repellency (% R) was calculated by the following formula.

$$ \%\mathrm{R}=\left[100\ \left(C-T\right)/C\right] $$

where C is the number of flies trapped in the control flask and T indicates the number of flies trapped in the treated flask.

Pupicidal bioassay

Pupicidal bioassays were carried out by following the method described by Kumar et al. (Kumar et al., 2011) with slight modifications. The bioassays were performed with 20 pupae (3 days old) in a 250-ml conical flask. The pupae were exposed to different doses in the range of 20 μl/0.25 l to 100 μl/0.25 l of air to assess the effect of fumigation through impregnation on a cotton swab. In control treatment, the pupae were exposed to acetone only. These pupicidal assays were performed at 28 ± 2 °C and RH 65 ± 5%. The observation was recorded till the 6th day after exposure to EOs during which emergence into adults was documented. These assays were carried out with five or more independent replicates. The percent inhibition rate (% IR) on pupal emergence was calculated by using the below given formula no. 4.

$$ \%\mathrm{inhibition}\ \mathrm{rate}=\mathrm{Cn}-\mathrm{Tn}/\mathrm{Cn}\times 100 $$

where Cn represents the number of newly emerged insects in the control set and Tn depicts the number of insects emerged after treatment.

Effect of essential oil on biochemical aspects of housefly larvae

In larvicidal bioassays, 10 individuals of third instar larvae of the fly were exposed to LC50 concentrations of essential oil for 24 h. After the treatment, the exposed larvae were collected and subjected to biochemical analyses such as determination of total sugars, glycogen, lipids, and proteins by following the Anthrone method specified by Plummer (Plummer, 1988). However, proteins and lipids were estimated by the methods of Bradford (Bradford, 1976) and Van Handel and Day (Van Handel & Day, 1988), respectively. Results obtained were analyzed with one-way ANOVA, followed by Tukey’s test (mean comparison) using GraphPad software version 3.6.

Enzyme assays

Different enzyme assays were carried out by treating the larvae with LC50 concentration approximately as described in the larvicidal bioassay. The whole guts of the treated larvae were suspended in lysis buffer and homogenized on ice using a glass homogenizer. The homogenate was centrifuged at 10,000 rpm for 10 min at 4 °C. The supernatant obtained was treated as enzyme extract and used for different enzyme assays. The α-amylase activity was determined by dinitrosalicylic acid (DNSA) procedure described by (Bigham et al. 2010), using 1% (w/v) starch as substrate. Briefly, 20 μl of the enzyme extract was mixed with 50 μl of PBS (pH 7.4) and 25 μl of 1% starch solution (w/v). The mixture was incubated at 35 °C for 30 min to allow the reaction to occur which was subsequently terminated by adding 85 μl DNSA reagent. The terminated reactions were heated in a boiling water bath for 10 min. Similarly, α- and β-glucosidase activities were determined by measuring the amount of p-nitrophenol released from 5 mM p-nitrophenyl–α–d-glucopyranoside and p-nitrophenyl–β–d-glucopyranoside, respectively. Here the assay mixtures were incubated at 25 °C for 30 min followed by termination with 100 μl of NaOH (0.1 M) solution. The absorbance was read spectrophotometrically at 540 nm, and the reducing sugars released were estimated by using glucose as standard.

Inhibition of acetylcholinesterase (AChE) activity

To determine the acetylcholinesterase (AChE) activity caused by the EO treatment, the sample preparation was carried out as described above except in place of the whole gut only head regions were taken for inhibition analysis. The activity was assayed by the modified method of Ellman and colleagues (Ellman et al., 1961). Briefly, 10 μl of enzyme extract was mixed with 10 μl deionized water, incubated at room temperature for 15 min followed by addition of 20 mM acetylthiocholine iodide and 10 μl of 0.5 M DTNB [5,5′-dithiobis (2-nitrobenzoic acid)]. The control was treated by taking acetone in place of the enzyme extract. The absorbances were recorded at 412 nm, and enzyme activity was measured in U/min/mg of protein.

Gas chromatography-mass spectrometric (GC-MS) analysis of essential oil

The chemical composition of tested EO was analyzed by gas chromatography-mass spectrometric (GC-MS) method. The liquid phase used in the chromatographic procedures helps to characterize the oil constituents responsible for the insecticidal property of the oils. For GC-MS, analysis of bay EO was carried out by the method of Peris and Blazquez (Peris & Blázquez, 2015). The column temperature in the program was 60 °C during 5 min, with 6 °C/min increase up to 180 °C, followed by a 20 °C/min increase up to 280 °C, which was maintained for 10 min. The carrier gas used was helium at a flow rate of 1 ml/min and a split ratio of 1:30. The analysis was performed using a GCMS-TQ8030 apparatus, equipped with RTX 5MS column. Finally, the component identification was elucidated based on the comparison of their relative retention time and mass spectra analysis with those of NIST11 library data (GC-MS system), and available literature.

Field emission scanning electron microscopy (FESEM)

In order to have a clear and discernible observation of the effects of oil treatment on larval body, 10 larvae of the third instar stage were treated with LC50 concentration of tested EO. The sacrificed (treated) larvae and control larvae were prepared for FESEM visualization by using the protocol of Kumar et al. (Kumar et al., 2011) with few modifications to compare the structural changes caused by the oil treatment. The specimens were primarily fixed in 2.5% glutaraldehyde (v/v) in distilled water for 15–17 h. Thereafter, sample specimens were washed with distilled water for 20 min, followed by fixation in 4% osmium tetroxide for about 2 h. The samples were washed with deionized water for 20 min and then dehydrated serially with different grades (30, 50, 70, 90, and 100% v/v) of alcohol each for 10 min. After dehydration, samples were subjected to critical point drying (CPD) in hexamethylenedisilazane (HMDS). The specimens were mildly coated with gold (100 Å) followed by observation at a voltage of 5.0 kV in a FEI NOVA Nano SEM (NPEP303, FEI USA).

Statistical analysis

Data obtained was subjected to statistical analysis. Results were reported as mean ± standard error means (SEM) of five or more independent replicates which were subjected to one-way ANOVA using Tukey’s test (p < 0.001). The LC50 and LC90values with their 95% confidence limits were determined by probit analysis which helped to analyze the dose–mortality response (Finney, 1952). Analysis of data was carried out in SPSS software version 19 as well as Microsoft Excel (Microsoft office suite, 2013).


Larvicidal and adulticidal efficacy

The larvicidal assay carried out by the residual film method showed that LC50 concentration of the bay EO shows higher larval mortality at 4 mg/ml with an actual dose 0.0629 μg/cm2 which is a very low concentration. The results observed with the larvicidal assay are depicted in Table 1. However, the LC90 concentration of the EO was observed to be 9.231 mg/ml with an actual dose of 0.144 μg/cm2 (Fig. 1a). As the dose concentration of EO increases, the percent (%) mortality of the treated larvae also increased. The efficacy of the tested oil was very significant when compared with the control tests indicating short-term exposure of larvae to lethal doses can markedly increase their mortality over time, thereby reducing the number of viable adults, leading to possible significant diminution in overall population of M. domestica. The effect of tested doses of the EO on adult insects showed significant mortality (Fig. 1b) varying with the dose range. However, the LC50 and LC90 concentrations for adult mortality by bay EO were found to be 43.03 mg/dm3 and 84.42 mg/dm3, respectively (Table 1).

Table 1 Larvicidal and adulticidal activities of bay essential oil on M. domestica
Fig. 1
figure 1

Bioefficacy of bay essential oil against M. domestica. a Percent mortality of larvae after a treatment of 24 h. b Adulticidal activity of the tested EO against newly emerged M. domestica after 24-h treatment. LC50 and LC90 are lethal concentrations at which 50% and 90% population dies, respectively. Each value represents the mean of five replicates. Asterisk indicates significance at p < 0.05

Attractant/repellant bioassay

The EOs derived from plants are volatile, natural, and complex organic compounds characterized by a strong odor formed as secondary metabolites. The repellency potential of the EO from L. nobilis was evaluated against housefly in glass chambers. In this assay, EO showed 27.58% repellency at a concentration of 0.1% (Table 2). Among the tested essential oil concentrations, 0.5% was found to be the most effective with 100% repellency whereas no repellency was observed on a dose of 0.1% after 1 h of continuous observations. The repellency potential of EO doses followed the pattern 0.1% > 0.5% > 1.0%. The tested laurel oil elicited a strong and abrupt effect against the adults of M. domestica at concentrations higher than 0.5% indicating 0.5% sufficient for 100% mortality of the flies.

Table 2 Percent (%) inhibition repellency of the adult houseflies by different doses of the EO using the fumigation method

Pupicidal bioassays

The pupicidal assay carried out by fumigation and contact toxicity protocols against the tested organism exhibited significant variation in growth inhibition with different doses of the bay EO (Table 2). The results of the fumigation assay revealed that a LD50 dose of bay EO for the pupal death was 64.09 μl/0.25 l of air (Fig. 2) whereas LD90 concentration was found to be over 104.35 μl/0.25 l of air. In case of higher doses, a complete inhibition of pupal emergence was noted (Additional file 1: Figure S1). Further, the increase in the dose concentration caused increased percent inhibition rate (PIR) which eventually lead to the deformities in adults in case of survived pupae. Similarly, in contact toxicity, we found that not a single pupa can transform into adult successfully at all tested doses indicating 100% mortality of the pupae.

Fig. 2
figure 2

Pupicidal assay showing percent (%) mortality of M. domestica larvae by fumigation method with bay EO. Significant *p < 0.001 when compared with the control. Each value represents the mean of five replicates

Effect of EO on biochemistry of housefly

The secondary metabolites of the plant origin cause a diverse effect on the metabolism of the insects. Therefore, we tested the effect of different concentrations of the bay EO on the larvae of housefly. The inferences of the present study elucidate that LC50 dose of the bay EO induced marked reduction in the level of total protein content of the treated larvae as compared with the control set. Further, the biochemical assays revealed that bay EO showed notable changes in total sugar, glycogen, lipid, and protein contents of third instars of M. domestica (Table 3). The tested oil remarkably reduced the total sugar content from 3.169 ± 0.191 μg/larva in the control to 0.448 ± 0.036 μg/larva in the treated larva. Not only sugars, the treatment also reduced total glycogen content, i.e., 0.117 ± 0.007 μg/larva after treatment comparable to normal larva (7.302 ± 0.131 μg/larva). A similar trend was observed with lipid content of the insect where its amount was decreased from 1400.2 ± 38.87 μg/larva in normal individual to 474.62 ± 57.35 μg/larva after treatment. In case of total protein content of the treated and control larvae, the proteins were significantly reduced from 1000.6 ± 11.47 μg/larva to 636.72 ± 26.98 μg/larva due to EO treatment.

Table 3 Effect of bay EO on nutritional reserves of M. domestica larvae

Effect of EO on gut enzymes

Since digestive tract is the main interface between insect and the environment, given that nutrition is a decisive factor in the evolutionary process of these organisms, the main aspect of the pest control is the selective inhibition of digestive enzymes secreted by the alimentary canal of pests. Keeping that in mind, we checked the effect of tested EO on gut enzymes such as α-amylase, α and β-glucosidases. There was a significant difference (Fig. 3a–c) in enzyme activities between treated and control larvae in case of both the enzymes under consideration showing a p < 0.001 only. The bay essential oil significantly decreased α-amylase activity (0.092 ± 0.002 μg/larva) when compared with control test (0.214 ± 0.004 μg/larva). We observed a substantial decrease of 57.1% in the activity of α-amylase indicating the effect of bay EO on M. domestica. Similarly, the effect of EO on α-glucosidase showed considerable reduction (1.878 ± 0.043 μg/larva) in its secretion by fly larvae as compared with control set (l2.375 ± 0.074 μg/larva) marking a difference of 21%. It also showed 1.3-fold reduction in β-glucosidase activity from 3.066 ± 0.071 μg/larva to 2.19 ± 0.024 μg/larva after treatment with the EO (Additional file 1: Table S1). The tested EO significantly affected the α-amylase of the gut extract upon treatment showing a decrease of over 51% activity (Fig. 3a).

Fig. 3
figure 3

Effect of bay essential oil on the gut enzymes of M. domestica larvae. a α-Amylase, b α-glucosidase, and c β-glucosidase activities of M. domestica. Values are means ± SE (standard error). Data analyzed by one-way ANOVA, followed by Tukey’s test and significance at *p < 0.001 compared with the control

Acetylcholinesterase (AchE) activity

As shown in Additional file 1: Figure S2, the bay EO was found to inhibit the AchE activity of M. domestica larvae after 24 h of treatment. The AchE activity in treated larvae was 0.0093 U/mg of protein compared with control larvae where it was much higher (0.013 U/mg of protein) indicating significant reductions caused by the exposure to EO.

GC-MS analysis of essential oil

The GC-MS analysis of the bay EO revealed an abundance of seven major components (Fig. 4). The components observed (Table 4) were terpenes such as myrcene, linalool (3, 7-dimethyl-1, 6-octadien-3-ol), and diterpenoids (E,E,E)-3,7,11,15-tetramethylhexadeca-1,3,6. Some of the phenolic compounds observed were eugenol, chavicol (phenol,4- (2-propenyl)) and anethole. The highest amount found was of the eugenol (58.95%) which proved to be the main component followed by phenol (13.96%), tetra methyl hexadeca (10.57%), and β-myrcene (6.03%). The insecticidal property of this plant EO could be attributed majorly to eugenol content and to some extent linalool compound. However, the compounds like β-myrcene, eugenol, and linalool comprise only about 3% of the total chemical compounds present in this plant.

Fig. 4
figure 4

Chromatogram obtained from GC-MS/MS analysis shows the chemical composition and abundance of some compounds of the bay EO

Table 4 GC-MS analysis of bay essential oil revealing the abundance of certain compounds

Field emission scanning electron microscopy (FESEM)

In order to clearly visualize the effect of EO treatment on the larval body surface, we employed FESEM technique to compare the ultra-structural changes in larval integument due to EO treatment with normal larvae. Upon analysis, a clear observation showed the toxic effect of bay oil in the form of integument shrinkage particularly at spinose rings with distorted intersegmental regions. However, control/normal larvae of M. domestica showed normal appearance with a smooth textured integument and well-shaped intersegment spines (Fig. 5a–c). Therefore, it can be concluded from the observed results that fly larvae upon contact with EO show superficial alterations to the integument.

Fig. 5
figure 5

The ultra-structural and superficial changes induced by bay EO to the larvae of M. domestica after a treatment for 24 h. a, c, and e show the anterior, posterior, and abdominal segments respectively of the control larva exhibiting normal appearance with smooth integument and well-defined or swollen intersegment spines, whereas b, d, and f show the FESEM micrograph anterior, posterior, and abdominal segments depicting the ultra-structural changes like shrinkage, rupture of body fluids, and corrugation of the integument induced by bay EO during treatment


Pesticides derived from plants are organic in nature, considered to be biodegradable, non-mutagenic or non-toxic to animals, and more particularly target specific than their chemically synthesized counterparts. Some of them also inhibit or reduce the insecticide detoxifying enzymes of the pests thereby could be important from the agriculture viewpoint (Wang et al.,2016). Therefore, keeping in mind the importance of plant-based EOs, we tested the efficacy of EO from L. nobilis against the different stages of the nuisance-causing housefly, M. domestica. We observed higher larval mortalities at very low doses of the compound which was only 0.0629 μg/cm2. The efficacy of Laurus EO against M. domestica as observed in this study is much higher than the insecticidal property of EOs derived from various other plants (Pavela, 2008). Recently, the efficiency of the EOs from L. nobilis has been tested on several other insects such as stored grain pests, where authors have suggested species-specific dose requirements for the control of pests (Drapeau et al., 2009; Pavela, 2008; Sertkaya et al., 2010). Ours is the pioneering study to report the effects of L. nobilis EO on the adults of M. domestica. Recently, Pavela and his colleagues (Pavela, 2008) tested more than 30 plant extracts against M. domestica and concluded that EO from Pogostemon cablin is the most efficient against fly at a concentration of 3 μg/fly which is quite higher than the concentration used in this study. Similarly, Asid and co-workers stated that Citrullus colocynthis extracts exhibit potential efficacy against all stages of M. domestica at 50% concentration (Asid et al., 2015). Previously, many authors have reported the antibacterial (Evrendilek, 2015), antifungal (Gumus et al., 2010), antioxidant (Inan et al., 2012), analgesic and anti-inflammatory properties (Sayyah et al., 2003), apart from some acaricidal (Senfi et al., 2014), larvicidal (Pavela, 2008), and insecticidal (Sertkaya et al., 2010) activities by laurel EO.

In order to ascertain the potential of bioactive compounds present in the bay EO, we used the GC-MS analysis that revealed dominance of eugenol and phenolic content which was in congruence with previous reports that have stated the chemical composition of the EO from the leaves of L. nobilis (Senfi et al., 2014; Sertkaya et al., 2010). Further insecticidal property of many compounds present in EO has been conducted topically by Rozman and co-workers (2007) wherein eugenol was found highly toxic to all tested beetles. Eugenol is also known to show higher repellency against beetles (Andronikashvili & Reichmuth, 2002; Huang et al., 2002; Rozman et al., 2007) and other stored grain pests (Cosimi et al., 2009; Lee et al., 2003). Further, these authors concluded the complete destruction of the eggs and immature stages of T. castaneum by eugenol. Our results were in line with Nehir et al. (2014) who found eugenol; 1,8-cineole; linalool; methyl eugenol; α-terpinyl acetate; α-pinene; and β-pinene as major components of laurel EO. Most of the terpenoids and phenols of plant origin have minimal vertebrate toxicity and are regarded as safe by United States Food and Drug Administration (USFDA). These compounds apparently cause hyperactivity, tremors, and convulsions followed by knockdown of pests similar to the symptoms by insecticides such as organophosphates and carbamates. However, previously similar signs have been described by insects upon exposure to pure monoterpenes (Coats et al., 1991). Some monoterpenes alter the physiological functions by competitive inhibition of acetylcholine esterase in houseflies and cockroaches (Grundy & Still, 1985; Ryan & Byrne, 1988). The toxic effects exerted by EO of L. nobilis could be attributed to the toxic constituent like eugenol, linalool, myrcene and other phenolic compounds present therein. Besides the fumigant and repellent activities of bay EO against M. domestica, it has also proven insecticidal against red flour beetle, T. castaneum (Cosimi et al., 2009; Lee et al., 2003). Further, monoterpenoids abundantly distributed in EOs of aromatic plants are lipophilic in nature thereby intervene with metabolic, biochemical, physiological, or behavioral functions of insects (Brattsten et al., 1983).

Similar to our study, Palacios et al. (2009b) examined the efficacy of EOs from several medicinal and edible plants against housefly and stated that orange peel and eucalyptus leaves are the most toxic to flies which had limonene (92.5%) and 1,8-cineole (56.9%), as the principal compounds. However, Kumar and co-workers (Kumar et al., 2011) have observed that EOs of Mentha piperita and Eucalyptus globules are the most effective plant extracts against M. domestica showing both repellent and insecticidal properties. From time immemorial, plant-derived substances have been used to repel or kill mosquitoes before the advent of synthetic chemicals (Curtis et al., 1990). The tested EO also showed higher repellency against adult flies preventing them from oviposition in the nearby vicinity which is also stated by other researchers against rust-red flour beetle Tribolium castaneum (Andronikashvili & Reichmuth, 2002), Sitophilus zeamais, Cryptolestes ferrugineus, Tenebriomolitor (Cosimi et al., 2009), and adult females of Culex pipiens (Erler et al.2006). The repellency of these compounds appears due to the presence of volatile monoterpenoids (Buescher et al., 1982; Curtis et al., 1990; Rutledge et al.,1983). Besides, Papachristos and Stampoulos (2002) showed that EO from bay plant presented a repellent activity against Acanthoscelides obtectus.

The pupicidal effect exerted by the tested EO was also significant for the bio control of housefly. Besides various fumigant and repellent activities of bay leaf EO against stored grain pest (Cosimi et al., 2009; Lee et al., 2003), there are few reports available about the insecticidal potential of bay leaf oil and its fractions against T. castaneum. In the present study, significant mortality or inhibition of pupal emergence was observed by both contact and fumigation pupicidal bioassays. In contrast, Kumar et al. (2011) observed 100% mortality of the same insect by contact toxicity method only.

Since most insects feed on carbohydrate-rich food products such as seed, fruits, crops, and stored grains, their guts are efficient natural biochemical reactors secreting a suite of hydrolytic enzymes such as amylase and α- and β-glucosidases. These enzymes hydrolyze α-d-1, 4-glucan linkages of starch, glycogen, and some other carbohydrates (Ferreira & Terra, 1989; Strobl et al., 1998). The amylase enzyme transforms starch into maltose, which is then converted to glucose by α-glucosidase and thus utilized as an energy source by the insect. In insects, only α-amylases have been found to hydrolyze long α-1, 4-glucan chains of starch or glycogen (Terra et al., 1988). Likewise, α-glucosidases break non-reducing 1, 4-linked α-d-glucose ends of glycogen whereas β-glucosidases catalyze the hydrolysis of β-glycosides into respective monosaccharides (Sezginturk & Dinckaya, 2008). Many insects are known to show β-glucosidase activities required for metabolism of ingested food such as Diatraea saccharalis (Azevedo et al. 2003) and Parnassiusapollos sp. (Nakonieczny, Michalczyk, & Kedziorski, 2006). The tested EO depicted neurotoxic effects by inhibiting AchE activity of the M. domestica larvae after 24 h of treatment with LC50 doses only. Many secondary metabolites such as EOs and monoterpenes of aromatic plants are known to inhibit the AchE activity of insects (Senthilm et al., 2008). Our observations were in accordance with Rajashekar and co-workers (2014) who concluded the inhibition of AchE in M. domestica by Coumaran, extracted from L. camara. Therefore, for designing a biocontrol strategy, it becomes imperative to understand the interaction of pesticide with digestive enzymes and AchE of the target organism. Hence we determined the effect of EO on gut enzymes of M. domestica where drastic changes in expression levels were observed. The treatment with EO reduced the activities of the α-amylase and α- and β-glucosidases by 57.1, 21, and over 30%, respectively, in treated larvae as compared with larvae without treatment (control).

The reduction in enzyme activity could be a consequence of the cytotoxic effect of plant compounds on epithelial cells of the gut that are responsible for the synthesis of α-amylase (Hichri et al.t, 2019). Cytotoxicity appears to include membrane damage by causing coagulation of the cytoplasm (Gustafson et al., 1998) thereby damaging its lipid and protein contents (Ultee et al., 2000) or disrupting cell membrane leading to leakage of macro molecules and ultimately cell lysis (Oussalah et al., 2007). Some plant EOs are also known to form stable complexes with digestive enzymes, making dissociation difficult. In case of biochemical contents, decreased levels of proteins, lipids, and glycogen were observed due to treatment of EO which could be primarily due to blocking of gut hydrolases, which leads to poor nutrient utilization, retarded growth, and consequent death by starvation (Jongsma & Bolter, 1997). However, the reduction in body protein content may be attributed to inhibition of DNA and RNA synthesis at molecular levels which then reflects the decrease in enzymatic activities. Our results were in congruence with earlier reports (Nathan et al., 2005) where authors have stated similar reduction in protein and metabolite contents in moth, Cnaphalocrocis medinalis, after treatment with plant compounds. The changes in total lipid contents were also caused by the treatment of EOs. Some authors have suggested that decreased lipid content may be a result of transformation of lipids into proteins to substitute the reduction in protein content or produce supplementary energy to combat the chemical stress. Hence, treatment with EOs might have interrupted this process and resulted in larval mortality.

The biochemical and metabolic disruption by the EO treatment was also superficially revealed by the FESEM analysis where a complete distortion of the body was observed. Our inferences were supported by the conclusion of Insun et al. (1999) who demonstrated the damage to the surface morphology of mosquito larvae by Kaempferia galangal extract. Moreover, the effect of monoterpenes on insect morphology was also investigated by Sukontason et al. (2004) who studied the structural changes induced in housefly larvae through SEM analysis after the application of eucalyptol oil. The authors reported significant deformation in the integument, inter segmental spines, and bleb formation of the treated larvae. The FESEM analysis of the treated larvae revealed extreme dehydration and surface distortion compared with the undisturbed, free, and smooth surface of control larvae, therefore confiraffirming the effect of tested EO on housefly larvae. The above all results of the presented research indicate that EOs from medicinal plants such as L. nobilis could be a potential alternative for use as housefly fumigants, provoking death of the insect within a short period of time.


The housefly is a cosmopolitan home invader linked to poor hygiene and low socioeconomic status. The search for new, highly selective, biodegradable insecticides is mandatory to solve the problem of residual toxicity to the environment, fauna or flora. Nature provides many products acting as an excellent alternative; among these are the botanical insecticides. With the recent rise of the green insecticide concept and increased public awareness, several attempts to use indigenous plants extracts as potential alternatives have been done, but only few plant-based control products appear in the market. This study recommends the usage of bay-based products in domestic botanical anti-fly insecticides, as it is ethnobotanical, endemic, safe, cheap, and available all year. Therefore, we should overcome barriers in industrialization, commercialization, and creation of market opportunities along with peoples’ awareness of its usage.

Availability of data and materials

All the data generated from this study is included in the paper and can be accessed from the corresponding author upon request approval.





Analysis of variance


Critical point drying


Dichlorodiphenyl trichloroethane


3,5-Dinitrosalicylic acid


5,5′-Dithiobis, 2-nitrobenzoic acid


Essential oil


Field emission scanning electron microscopy


Gamma amino butyric acid


Gas chromatography-mass spectrometry/mass spectrometry




Lethal concentration


Lethal dose


Sodium hydroxide


National chemical laboratory


Phosphate-buffered saline


Percent inhibition rate


Relative humidity


Scanning electron microscope


Standard error means


United States Food and Drug Administration


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JC is highly indebted to the authorities of the S.P. Pune University, Pune, India, for providing the research stipend. MD is grateful to the University Grants Commission (UGC), New Delhi, India, for senior research fellowship under the Maulana Azad National fellowship scheme. RSP acknowledges the UPE-II (nanobiotechnology), UoP-BCUD grant (15-SCI-001422), and DRDP and DST-PURSE schemes provided to the laboratory.


The work was supported by Savitribai Phule Pune University, Pune, under the project code UoP-BCUD grant (15-SCI-001422), as well as DRDP and DST-PURSE schemes provided to the RSP.

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JC and RSP conceived and designed the experiments. JC and MD performed the experiments. JC, MD, and RSP wrote the paper. All authors read and approved the final manuscript.

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Correspondence to Mudasir A. Dar or Radhakrishna S. Pandit.

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Additional file 1: Figure S1.

Histogram depicting percentage inhibition rate (PIR) against housefly pupae in a fumigation toxicity assay by Bay EO. N: normally emerged adult; DE: deformed pupa/adult; D: dead pupae. Significant * p < 0.001 when compared to control. Figure S2. Inhibition of Acetylcholinesterase activity by bay EO after 24 hr of treatment. Significance at *p < 0.001 compared with control). Table S1. Effect of bay EO on the gut/digestive enzymes of the M. domestica larvae. Value are mean ± SE (Standard error). Data were analyzed by One-Way ANOVA, followed by Tukey’s test and Significance at *p < 0.001 compared with control.

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Chintalchere, J.M., Dar, M.A. & Pandit, R.S. Biocontrol efficacy of bay essential oil against housefly, Musca domestica (Diptera: Muscidae). JoBAZ 81, 6 (2020).

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