<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">AE</journal-id><journal-title-group><journal-title>Advances in Entomology</journal-title></journal-title-group><issn pub-type="epub">2331-1991</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ae.2022.104022</article-id><article-id pub-id-type="publisher-id">AE-120343</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Potential Insecticidal Effect of a Wasp (&lt;i&gt;Polistes dominulus&lt;/i&gt;) and a Bee (&lt;i&gt;Apis mellifera&lt;/i&gt;) Venoms in Controlling &lt;i&gt;Spodoptera littoralis&lt;/i&gt;
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Reham</surname><given-names>Z. Sadek</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Shereen</surname><given-names>M. El Banna</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Fayez</surname><given-names>M. Semida</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Samy</surname><given-names>M. Zalat</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Zoology Department, Faculty of Science, Suez Canal University, Ismailia, Egypt</addr-line></aff><pub-date pub-type="epub"><day>27</day><month>07</month><year>2022</year></pub-date><volume>10</volume><issue>04</issue><fpage>300</fpage><lpage>319</lpage><history><date date-type="received"><day>10,</day>	<month>August</month>	<year>2022</year></date><date date-type="rev-recd"><day>8,</day>	<month>October</month>	<year>2022</year>	</date><date date-type="accepted"><day>11,</day>	<month>October</month>	<year>2022</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  Cotton leaf worm, 
  Spodoptera littoralis, is considered one of the most common arthropod pests that contribute to crop devastation of cotton. Previously, agricultural pests were controlled through the application of chemical insecticides. However, insecticide-resistant insect populations emergence, as well as increasing concerns about the environmental and human health risks. Venomous animals introduce valuable sources of bioactive compounds which are employed for defence. Some of these toxins have high phyletic specificity, making them appropriate for use in IPM programs. This study aims to test the insecticidal effects of 
  Polistes dominulus and 
  Apis mellifera venoms. Crude venoms were examined for their insecticidal effect against cotton leaf worms by four different application methods including: leaf dipping, integument dropping, spraying, and injection. The data demonstrated a strong response to purified (
  Polistes dominulus) venom at an initial time than that of honey bee (
  Apis mellifera) which increases response with increasing the dose and the time interval. A dosage of 0.015 - 0.16 ml of both venoms had notably varied in LD
  <sub>50</sub> values on 
  Spodoptera littoralis that showed higher wasp venom toxicity. Cotton leaf worms showed more susceptibility and mortality to the 
  Polistes sp. venom than that of honey bees.
 
</p></abstract><kwd-group><kwd>Social Insects</kwd><kwd> Honey Bee</kwd><kwd> Yellow Jacket</kwd><kwd> Enzymes</kwd><kwd> Pest Control</kwd><kwd> Bio-Insecticides</kwd><kwd> Biological Control</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Pests cause great damage to crop plants in Egypt, larvae of these pests can feed on ≈90 economically important plant species belonging to 40 families. Spodoptera littoralis (Boisd.) is a severely destructive insect pest of cotton. The widespread use of pesticides to control S. littoralis larvae has resulted in environmental and health issues and risks, including resistance development and residual effects [<xref ref-type="bibr" rid="scirp.120343-ref1">1</xref>].</p><p>Chemical pesticides are primarily used to control agricultural insect pests as well as insect vectors of major human diseases. However, the usage of chemical pesticides has resulted in a number of issues, including degradation of the environment and a rise in human health impacts. Secondary pest outbreaks focused on using bio-insecticides as chemical alternatives.</p><p>Efforts were focused on finding new control agents with new modes of action. These substances are pesticides that are selective and particular to the pest in concern. [<xref ref-type="bibr" rid="scirp.120343-ref2">2</xref>] elicits their primary action on insect mortality, and metabolism and ultimately affects the development and growth of the target insect. They induce morphological abnormalities as well as the death of treated insects. These characteristics allow the most promising new control agents for controlling S. littoralis larvae.</p><p>For decades, scientists have been curious by the secretions of venomous creatures. The modern era of molecular toxicology was fueled by a desire to purify and understand the mechanism of action of lethal components from medically important animals like marine cone snails [<xref ref-type="bibr" rid="scirp.120343-ref3">3</xref>], stonefish [<xref ref-type="bibr" rid="scirp.120343-ref4">4</xref>], insects, and snakes [<xref ref-type="bibr" rid="scirp.120343-ref5">5</xref>]. In the late 1980s and early 1990s, pioneering work by [<xref ref-type="bibr" rid="scirp.120343-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref8">8</xref>], and others led to an understanding that most animal venoms are made up of a complex cocktail of peptide and protein components, the fatal toxin being only one of them, represents only a minor proportion. Furthermore, it became clear that many of the non-lethal venom components have useful bioactivities that allow them to be used as research tools, such as in the characterization of ion channels [<xref ref-type="bibr" rid="scirp.120343-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref9">9</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref11">11</xref>], or as leads for the development of pharmaceutical agents [<xref ref-type="bibr" rid="scirp.120343-ref12">12</xref>] and insecticides [<xref ref-type="bibr" rid="scirp.120343-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref14">14</xref>].</p><p>The majority of research has been carried out on isolating pesticide toxins with bio-control action. Hymenoptera venoms were selected because of their relevance as a model for social and solitary insects, respectively, as well as their taxonomic relationship to economically important pest insects.</p><p>Various chemical cocktails are produced by venomous animals for defence, prey acquisition, competitor deterrence, and/or extra-oral digesting [<xref ref-type="bibr" rid="scirp.120343-ref15">15</xref>]. With some venoms containing over 1000 distinct peptides, these venoms have shown to be a valuable source of pharmacologically active chemicals [<xref ref-type="bibr" rid="scirp.120343-ref16">16</xref>]. While some of these peptides have been shown to be invertebrate-specific [<xref ref-type="bibr" rid="scirp.120343-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref17">17</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref19">19</xref>], many venom toxins exhibit activity in a wide range of phyla, therefore, the careful selection of peptides tracked for commercial pesticide manufacture is required [<xref ref-type="bibr" rid="scirp.120343-ref20">20</xref>]. However, some of these toxins may be ideal for use in IPM programmes due to their high phyletic specificity.</p><p>The venom characteristics and components of solitary and social bees and wasps are believed to differ depending on their social activity. Although it has been assumed to have more diversified bioactive components with pest inactivation and physiological manipulation capabilities, there are just too little data on the venom compositions of social and solitary wasps and bees to make this assumption. However, several neurotoxic peptides and proteins appear to be unique to the venoms of solitary bees and wasps in addition to several other bioactive proteins.</p><p>Venom components target the main critical systems of an organism, such as biological, neuromuscular, and hemostatic systems, to achieve the most efficient and rapid immobilization or death of the victim. Since venomous animals prey on many different species, as well as have a defense system against unspecified intruders, they produce various effects and mechanisms both with specific molecular targets and those that are active across a wide range of animal species. Bee venom is made up of a complex mixture of proteins, peptides, and low-molecular-weight components. Its constituents have been identified and classified in recent years. Phospholipase, Hyaluronidase, Phosphatase, and Glucosidase are some of the most important components [<xref ref-type="bibr" rid="scirp.120343-ref21">21</xref>]. Wasp venoms, on the other hand, are made up of a complex mix of proteinacious and non-proteinacious components that could be used as agrichemicals or pharmaceuticals to help with pest control.</p><p>Similarly, preliminary research indicates that infected cotton worm pests with venom might have a reduced propensity to feed prior to death [<xref ref-type="bibr" rid="scirp.120343-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref18">18</xref>] and there is evidence that bee and wasp venoms can affect not only the pest mortality, but also the survivorship [<xref ref-type="bibr" rid="scirp.120343-ref18">18</xref>]. The mechanisms that underlie this effect are unknown but might include alterations in host nutritional balance, which lead to resource competition, upregulation of immune responses, or production of secondary metabolites in the haemolymph.</p><p>The purpose of this research was to create a bioassay method that would allow new active bio-insecticides to be discovered using the venom of bees and wasps. When venom amounts are treated on cotton worms, which are considerably more sensitive to insect venoms, provides a better bioassay for the development of new insecticidal toxins.</p><p>Therefore, this study aims to: investigate the possible insecticidal activity of crude venom of bees and wasps against cotton leaf worm pest and investigate some of the biological mortality, toxicological and morphological effects of the venom components on cotton leaf worm.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Biological Studies</title><p>Polistes dominulus and Apis mellifera species were collected. The individuals were caught and subjected to a low-temperature, ice-controlled environment right away. To euthanize wasps and bees, freeze them for 5 hours at −20˚C.</p><p>Venom was obtained from poison glands of both social bees and wasps, and poisonous secretions were separated from venom glands using dissection instruments, a light microscope, were used to extract venoms from 208 wasp venom sacs, which were meticulously dissected from the wasps, macerated in a 1:1 (v:v) acetonitrile/water solution, and centrifuged at 5000 g for 5 minutes at room temperature and vacuum drying. The supernatant was collected, vacuum dried, weighed in a precision balance, and stored at 20˚C. Lipholization was used to obtain venom powder, vacuum drying the venom in silica gel.</p></sec><sec id="s2_2"><title>2.2. Rearing Technique of Cotton Leaf Worm, Spodoptera littoralis</title><p>A laboratory strain of S. littoralis was reared in the laboratory away from any insecticidal contamination at the Department of Cotton Leaf Worm, Branch of Plant Protection Research Institute at Zagazig, Sharqia Governorate under constant conditions 25˚C &#177; 2˚C and 60% &#177; 5% R.H. to provide insects used in the present investigation. Egg-masses were placed on leaves of castor bean oil, Ricinus communis in cylindrical glass jars (El-Defrawi et al., 1964).</p><p>After egg hatching, the newly hatched larvae were transferred into large rearing jars and provided with filter paper at the bottom of the jars to absorb excess moisture. Larvae were reared on fresh castor bean leaves until the end of larval stage. The formed pupae were collected and placed in clean jars until adult emergence. Each jar was provided with 10% honey solution soaked in cotton wool, which was renewed daily to avoid fermentation and growth of microorganisms. Fresh green castor leaves were introduced daily into clean jars.</p></sec><sec id="s2_3"><title>2.3. Venom Application Experiments</title><p>Preliminary tests for each of the separate treatments were conducted using a variety of concentrations (in distilled water) for each of the venom concentrations (0.01, 0.02, 0.04, 0.08, 0.16 &#181;l). Cotton worms were treated in glass jars with various concentrations of bee and wasp venoms then provided to early 4<sup>th</sup> instar larvae to pupate on. According to [<xref ref-type="bibr" rid="scirp.120343-ref22">22</xref>], the offered treated larvae were in a wettable state, and the leaf-dipping strategy was used. Castor bean leaves (R. communities) were dipped in each concentration and dried at room temperature before being fed to newly moulted 4<sup>th</sup> instar larvae. The larvae were allowed to feed for 24 hours before being fed new, untreated castor bean leaves until pupation. Controls for bee and wasp treatments were larvae that ate untreated castor bean leaves. For each concentration, eight replicates were carried out, with each replicate containing five larvae. The percentages of larval mortality and morphological deformity were calculated. The data were then subjected to probit analysis [<xref ref-type="bibr" rid="scirp.120343-ref23">23</xref>] to obtain the LC<sub>50</sub> values of both social bee and wasp venom as well as the concentration which causes 50% adult malformation (MC<sub>50</sub>). Measuring the mortality and morphological changes through cotton worm pest treated with different concentrations of social wasp and bee venom through topical food, integument dropping, injection and spraying applications.</p><p>Injection: Cotton worms between 3<sup>rd</sup> and 4<sup>th</sup> instar (90 - 110 mg/individual) were used for injections. 0.1 mL of venom diluted in insect saline was injected into the metathoracic pleurite, and for all five concentration till 1.6 mL were injected. Injections were performed using a 29.5 gauge insulin syringe (B-D Ultra-Fine, Terumo Medical Corporation, Elkton, MD, USA). A cohort of ten insects was injected at each venom concentration, and a similar number of control insects were injected with insect saline.</p><p>Integument dropping: Lyophilized crude bee and wasp venoms were tested for biological activity by topically dropping &#181;l of aqueous samples into newly eclosed fourth instar S. littoralis larvae (40 - 70 mg). For each concentration tested, 80 larvae were topically dropped on integument and toxic effects were monitored over 4 - 5 days.</p><p>Spraying: treatment doses are then harvested from the bees and wasps venom and formulated in acetone solvent for application using hand-held (panel d) or aerial-mounted sprayers.</p></sec><sec id="s2_4"><title>2.4. Morphological Malformations of Cotton Leaf Worm, Spodoptera littoralis</title><p>Honey bee venom as well as yellow jacket the concentration which causes 50% larval malformations (MC<sub>50</sub>) for cotton worm Spodoptera littoralis was measured. The sequential cumulative effect among treatments of cotton worm with either venoms were carried out by treatment of the 4<sup>th</sup> instar larvae with the considered concentrations in order to obtain MC<sub>50</sub> effects of Apis mellifera and Polistes dominulus then, at the end of larval stage, the late 6<sup>th</sup> instar larvae were allowed to pupate on castor bean treated with both venoms at which pupal MC<sub>50</sub> were estimated.</p></sec><sec id="s2_5"><title>2.5. Toxic Effects of Tested Venoms against Cotton Leaf Worm, Spodoptera littoralis under Laboratory Conditions</title><p>The effectiveness of various venom concentrations was tested on 4<sup>th</sup> instar larvae by application, topical on food, spraying, topical on integument, and injection. Using distilled water, serial successive concentrations of each venom were created, starting with the recommended concentration. Castor bean leaf discs (9 cm in diameter) were dipped in the tested concentrations for 10 seconds, dried, and fed to larvae that had been starved for 4 - 6 hours before treatment [<xref ref-type="bibr" rid="scirp.120343-ref24">24</xref>]. The larvae were placed in 5 pound glass jars, and each treatment was repeated eight times (5 larvae per each). Only distilled water was used to dip the control discs. The larvae were given 48 hours to feed on the treated discs before being moved to the untreated ones. For everyone, mortality percentages were obtained after 24, 48, 72, and 96 hours. Probit analysis was used to statistically examine the dose toxicity regression lines [<xref ref-type="bibr" rid="scirp.120343-ref23">23</xref>]. Sun formulae were used to compute the Toxicity Index and Relative Potency [<xref ref-type="bibr" rid="scirp.120343-ref21">21</xref>]. At the end of each testing period, total mortalities were determined and corrected using Abbott's formula [<xref ref-type="bibr" rid="scirp.120343-ref25">25</xref>].</p></sec><sec id="s2_6"><title>2.6. Mortality of Treated Cotton Leaf Worm, Spodoptera littoralis</title><p>Samples of cotton leaves were picked up at random for each treatment at zero time directly after applying with four different treatment methods for cotton worm insect pest S. littoralis through spraying, topical on food application, dropping on integument and direct injection. The prepared samples concentrations were sealed in small flasks and transferred to the laboratory where they were offered to cotton leaf worm larvae (Aly, 1999). Five larvae were placed in each glass jar and allowed to feed on the treated leaves for 1 to 5 days then the survived larvae were transferred to other clean jars and supplied with fresh clean castor bean leaves for another 3 days. Eight replicates were used for each treatment. Cumulative mortalities were calculated at the end of each testing time [<xref ref-type="bibr" rid="scirp.120343-ref26">26</xref>].</p><p>The mortalities at the zero time were considered as initial kill; while the mean of the cumulative mortalities of the remaining tested times were considered as cumulative final effect.</p></sec><sec id="s2_7"><title>2.7. Statistical Analysis</title><p>Data were subjected to statistical analyses using a software package CoStat<sup>&#174;</sup> Statistical Software (2005) a product of Cohort Software. The significance of the main effects was determined by analysis of variance (ANOVA) and chi-square tests. The significance of various treatments was evaluated by Duncan’s multiple range tests (P &lt; 0.05) [<xref ref-type="bibr" rid="scirp.120343-ref27">27</xref>].</p></sec></sec><sec id="s3"><title>3. Results</title><p>The current study showed advances in the development of bio-pesticides based on some Hymenoptera venom which involved successful development of bio pesticides for the control of cotton leaf worms to examine their potential on pest mortality, morphology, feeding and development.</p><sec id="s3_1"><title>3.1. Biological Studies</title>Morphological Malformation against S. littoralis<p>Two bio pesticides from social bee and wasp venom [Hymenoptera] (used at MC<sub>50</sub>, concentration caused more than 50% morphological malformation) were used for treatment of larvae of cotton leaf worm, Spodoptera littoralis. The obtained results revealed that wasp is a potent toxin (LC<sub>50</sub> ≤ 0.001 ppm) at initial time compared to bee venom (LC<sub>50</sub> = 0.49 ppm) when applied topically on food (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="table" rid="table2">Table 2</xref>).</p><p>On the other hand, the mode of action through morphological malformation, the malformation concentration fifty (MC<sub>50</sub> for cotton leaf worms treated by yellow jacket venom which was significantly higher at integument dropping and injection applications. All treatments caused higher significant morphological differences within integument, pores and dark bands when treated with Yellow jackets venom at final time interval.</p><p>The topical food application results revealed that wasp venom is a potent toxin causing morphological malformations that showed the highest effect on cotton leaf worm larvae while integument drooping highest effect was shown on the</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> LC<sub>50</sub> values for social bee venom on 4<sup>th</sup> instar larvae of cotton leaf worm S. littoralis LC<sub>50</sub> (&#181;l/g) showing different relative susceptibility evaluation of the tested insecticides</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Linear probit</th><th align="center" valign="middle" >Linear response%</th><th align="center" valign="middle" >Observed response%</th><th align="center" valign="middle" >Treated</th><th align="center" valign="middle" >Log (Conc. χ 100)</th><th align="center" valign="middle" >Conc. χ 100</th><th align="center" valign="middle" >Conc.</th></tr></thead><tr><td align="center" valign="middle" >3.8635</td><td align="center" valign="middle" >12.7925</td><td align="center" valign="middle" >17.949</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.4771</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >4.5191</td><td align="center" valign="middle" >31.5304</td><td align="center" valign="middle" >17.949</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6021</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >0.04</td></tr><tr><td align="center" valign="middle" >5.0272</td><td align="center" valign="middle" >51.0852</td><td align="center" valign="middle" >58.974</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6990</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.05</td></tr><tr><td align="center" valign="middle" >4.4479</td><td align="center" valign="middle" >29.0434</td><td align="center" valign="middle" >32.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.0000</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" >4.9128</td><td align="center" valign="middle" >46.5250</td><td align="center" valign="middle" >40.000</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.3010</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >5.1848</td><td align="center" valign="middle" >57.3286</td><td align="center" valign="middle" >57.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.4771</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >5.3779</td><td align="center" valign="middle" >64.7223</td><td align="center" valign="middle" >65.000</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6021</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >0.04</td></tr><tr><td align="center" valign="middle" >5.5275</td><td align="center" valign="middle" >70.1079</td><td align="center" valign="middle" >72.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6990</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.05</td></tr><tr><td align="center" valign="middle" >4.1929</td><td align="center" valign="middle" >20.9798</td><td align="center" valign="middle" >20.000</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.4771</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >4.3330</td><td align="center" valign="middle" >25.2413</td><td align="center" valign="middle" >27.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6021</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >0.04</td></tr><tr><td align="center" valign="middle" >4.4417</td><td align="center" valign="middle" >28.8326</td><td align="center" valign="middle" >27.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6990</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.05</td></tr><tr><td align="center" valign="middle" >4.3893</td><td align="center" valign="middle" >27.0683</td><td align="center" valign="middle" >37.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.0000</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" >4.7976</td><td align="center" valign="middle" >41.9800</td><td align="center" valign="middle" >37.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.3010</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >5.0365</td><td align="center" valign="middle" >51.4533</td><td align="center" valign="middle" >40.000</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.4771</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >5.2061</td><td align="center" valign="middle" >58.1625</td><td align="center" valign="middle" >50.000</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6021</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >0.04</td></tr><tr><td align="center" valign="middle" >5.3375</td><td align="center" valign="middle" >63.2109</td><td align="center" valign="middle" >87.500</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >0.6990</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.05</td></tr></tbody></table></table-wrap><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> LC<sub>50</sub> values for both social bee and wasp venoms on 4<sup>th</sup> instar larvae of cotton leafworm S. littoralis LC<sub>50</sub> (&#181;l/g) showing different relative susceptibility evaluation of the tested insecticides</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Linear probit</th><th align="center" valign="middle" >Linear response%</th><th align="center" valign="middle" >Observed response%</th><th align="center" valign="middle" >Treated</th><th align="center" valign="middle" >Log (Conc. χ 100)</th><th align="center" valign="middle" >Conc. χ 100</th><th align="center" valign="middle" >Conc.</th></tr></thead><tr><td align="center" valign="middle" >4.8614</td><td align="center" valign="middle" >44.4905</td><td align="center" valign="middle" >48.33</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.0000</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" >5.1696</td><td align="center" valign="middle" >56.7334</td><td align="center" valign="middle" >51.667</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.3010</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >5.3500<sup> </sup></td><td align="center" valign="middle" >63.6789</td><td align="center" valign="middle" >60.000</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.4771</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >5.4780</td><td align="center" valign="middle" >68.3638</td><td align="center" valign="middle" >70.000</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.6021</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >0.04</td></tr><tr><td align="center" valign="middle" >5.5772</td><td align="center" valign="middle" >71.8088</td><td align="center" valign="middle" >75.000</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.6990</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.05</td></tr><tr><td align="center" valign="middle" >5.9233</td><td align="center" valign="middle" >82.2030</td><td align="center" valign="middle" >83.333</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.0000</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" >6.0891</td><td align="center" valign="middle" >86.1911</td><td align="center" valign="middle" >83.333</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.3010</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >6.1861</td><td align="center" valign="middle" >88.2161</td><td align="center" valign="middle" >90.000</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.4771</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >4.6795</td><td align="center" valign="middle" >37.4306</td><td align="center" valign="middle" >33.333</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.0000</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" >5.0645</td><td align="center" valign="middle" >52.5709</td><td align="center" valign="middle" >51.667</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.3010</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >5.4497</td><td align="center" valign="middle" >67.3532</td><td align="center" valign="middle" >76.667</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.6021</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >5.8348</td><td align="center" valign="middle" >79.8062</td><td align="center" valign="middle" >80.000</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.9031</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >0.04</td></tr><tr><td align="center" valign="middle" >6.2198</td><td align="center" valign="middle" >88.8706</td><td align="center" valign="middle" >85.000</td><td align="center" valign="middle" >600</td><td align="center" valign="middle" >1.2041</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.05</td></tr><tr><td align="center" valign="middle" >4.8554</td><td align="center" valign="middle" >44.2541</td><td align="center" valign="middle" >48.333</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.0000</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.01</td></tr><tr><td align="center" valign="middle" >5.4352</td><td align="center" valign="middle" >66.8273</td><td align="center" valign="middle" >61.667</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.3010</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >5.7743</td><td align="center" valign="middle" >78.0625</td><td align="center" valign="middle" >71.667</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.4771</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >0.03</td></tr><tr><td align="center" valign="middle" >6.0151</td><td align="center" valign="middle" >84.4914</td><td align="center" valign="middle" >91.667</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >0.6021</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.04</td></tr></tbody></table></table-wrap><p>second level at morphological deformations. MC<sub>50</sub> = 0.0013 ppm compared to bee venom MC<sub>50</sub> = 0.0157 ppm, while integument dropping application showed MC<sub>50</sub> = 0.0114 ppm) compared to bee venom MC<sub>50</sub> = 0.0303 ppm). The spraying application of wasp venom showed MC<sub>50</sub> = 0.014 ppm on treated cotton leaf worms compared to bee venom MC<sub>50</sub> = 0.139 ppm. Finally the injection application was MC<sub>50</sub> = 0.0412 ppm compared to bee venom (MC<sub>50</sub> = 0.792 ppm) (<xref ref-type="fig" rid="fig1">Figure 1</xref> and <xref ref-type="fig" rid="fig2">Figure 2</xref>).</p><p>It was observed that venom applied by spraying has significant effect rather than by topical application. Spraying application of venom affect by black spots than topical application. Topical affect more by shrinkage of insect body while venom application by injection was observed to have the least morphological effect on cotton worm larvae.</p></sec><sec id="s3_2"><title>3.2. Toxicity of Bee and Wasp Venoms against S. littoralis through LC<sub>50</sub> Value</title><p>According to LC<sub>50</sub> and LC<sub>90</sub> values, topical application of bee venom was the most effective method where the LC<sub>50</sub> and LC<sub>90</sub> values recorded 0.1, 0.809 ppm for 4<sup>th</sup> instar treated with bee venom and 0.472 and 6.838 ppm for the 4<sup>th</sup> instars larvae treated with wasp venom, respectively.</p><p>Meanwhile, injection application appeared to be the least effective against pest tested instars, where the LC<sub>50</sub> and LC<sub>90</sub> values against 4<sup>th</sup> instar were 9.901 and 36.447 ppm for bee venom and the values against the 4<sup>th</sup> one were 65.736 and 1000.775 ppm for wasp venom, respectively.</p><p>The rest venom application methods gave moderate effects against instars that manifested, the LC<sub>50</sub> and LC<sub>90</sub> levels were 0.204 and 2.311 ppm for bee venom, 0.255 and 5.484 ppm for wasp venom. 1.001, 12.34 ppm for topical on integument application with bee venom and 9.901, 36.447 ppm for topical on integument application with wasp venom, respectively for 4<sup>th</sup> instar larvae (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="table" rid="table2">Table 2</xref>).</p><p>The social honey bee venoms killed cotton worms with LD<sub>50</sub> values in the range 69 - 126 mg/g, while the social Polistes sp. Wasp venom were slightly more potent, with LD<sub>50</sub> values of 46 - 48 mg/g (<xref ref-type="fig" rid="fig3">Figure 3</xref>). These values are comparable to the LD<sub>50</sub> value of 105 mg/g reported for injection of crude venom into 3<sup>rd</sup> - 4<sup>th</sup> instar Spodoptera littoralis. Thus, while there might be statistically significant</p><p>differences in potency between social bee and wasp venoms, it is remarkable that the LD<sub>50</sub> values of all of the venoms tested to date against cotton worm cluster in the range 69 - 242 mg/g.</p></sec><sec id="s3_3"><title>3.3. Mortality of Bee and Wasp Venoms against S. littoralis</title><p>Results indicated the important role of feeding period on treated leaves for 48 h followed by untreated leaves for 3 days. So, the evaluation was assessed using the cumulative mortalities. In this study mortality calculated after 72 hrs after each application of either social bee or wasp venom. The initial effect that (calculated as the cumulative mortalities at zero time) recorded 100%, 100%, 92%, 88% and</p><p>26% for spraying, topical on food, injection and on integument, respectively. Control recorded 1% mortality. Both topical application methods gave the highest significant mortalities compared to the control that manifested 0.76313 &#177; 0.43 and 0.921 &#177; 0.115 respectively for honey bee and 1.0169 &#177; 0.053 for wasp venoms (F<sub>(4,389)</sub> = 6.56; P &lt; 0.0001) (F<sub>(4,389)</sub> = 35.65; P &lt; 0.0001) (<xref ref-type="table" rid="table3">Table 3</xref> and <xref ref-type="table" rid="table4">Table 4</xref>).</p><p>Cotton worm treatment with bee venom has accordingly reduced survival times at concentrations (0.04, 0.08, 0.16 ppm). Reduced survival times have reached 87% and 72% for A. mellifera while it was higher reached 98 and 100% for Polistes sp. (<xref ref-type="table" rid="table4">Table 4</xref>). For topical application on food and integument drop when compared with control. Caterpillars infected by spraying bee venom demonstrated significant survival reduction effects (F<sub>(</sub><sub>4,389)</sub> = 25.59; P &lt; 0.00001) (F<sub>(4,389)</sub> = 5.12; P &lt; 0.0001) (<xref ref-type="fig" rid="fig3">Figure 3</xref>). It was low for both bee and wasp venoms effect on cotton worm mortality compared to infection by venom topical applications.</p><p>Topical application on food of bee venom indicated the mortality of S. littoralis was significantly different (χ<sup>2</sup> = 68.13; d.f. = 2; P &lt; 0.0001) among applications with highest number on Polistes sp. than A. mellifera but lowest mortality on injection of both bee and wasp venoms respectively (Figures 4(a)-(d), <xref ref-type="table" rid="table3">Table 3</xref> and <xref ref-type="table" rid="table4">Table 4</xref>).</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Effect of five different concentrations of bee venom on cotton worm Spodoptera littoralis mortality with different application methods of venom respectively</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="3"  >Conc. (&#181;l)</th><th align="center" valign="middle"  colspan="4"  >Application</th></tr></thead><tr><td align="center" valign="middle" >Spray</td><td align="center" valign="middle" >food</td><td align="center" valign="middle" >Integument</td><td align="center" valign="middle" >injection</td></tr><tr><td align="center" valign="middle" >(H.B)</td><td align="center" valign="middle" >(H.B)</td><td align="center" valign="middle" >(H.B)</td><td align="center" valign="middle" >(H.B)</td></tr><tr><td align="center" valign="middle" >C1</td><td align="center" valign="middle" >0.00 &#177; 0.00</td><td align="center" valign="middle" >0.34 &#177; 0.19</td><td align="center" valign="middle" >0.39 &#177; 0.20</td><td align="center" valign="middle" >0.00 &#177; 0.00</td></tr><tr><td align="center" valign="middle" >C2</td><td align="center" valign="middle" >0.00 &#177; 0.00</td><td align="center" valign="middle" >0.42 &#177; 0.20</td><td align="center" valign="middle" >0.42&#177; 0.20</td><td align="center" valign="middle" >0.00 &#177; 0.00</td></tr><tr><td align="center" valign="middle" >C3</td><td align="center" valign="middle" >0.21 &#177; 0.16</td><td align="center" valign="middle" >0.68 &#177; 0.20</td><td align="center" valign="middle" >0.49 &#177; 0.20</td><td align="center" valign="middle" >0.21 &#177; 0.16</td></tr><tr><td align="center" valign="middle" >C4</td><td align="center" valign="middle" >0.25&#177; 0.18</td><td align="center" valign="middle" >0.78 &#177; 0.19</td><td align="center" valign="middle" >0.52 &#177; 0.20</td><td align="center" valign="middle" >0.28 &#177; 0.18</td></tr><tr><td align="center" valign="middle" >C5</td><td align="center" valign="middle" >0.63 &#177; 0.19</td><td align="center" valign="middle" >0.86 &#177; 0.17</td><td align="center" valign="middle" >0.92 &#177; 0.11</td><td align="center" valign="middle" >0.39 &#177; 0.19</td></tr></tbody></table></table-wrap><p>Data represents the mean value &#177; S.E. from 25 cotton leaf worm/group with significance difference between the five different concentrations, using Chisquare test (χ<sup>2</sup> = 52.11, d.f. = 28, P ≤ 0.0037).</p><table-wrap id="table4" ><label><xref ref-type="table" rid="table4">Table 4</xref></label><caption><title> Effect of five different concentrations of bee venom on cotton worm Spodoptera littoralis mortality with different application methods of venom respectively</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="3"  >Conc (&#181;l)</th><th align="center" valign="middle"  colspan="4"  >Application</th><th align="center" valign="middle" ></th></tr></thead><tr><td align="center" valign="middle" >sray</td><td align="center" valign="middle" >Food</td><td align="center" valign="middle" >integument</td><td align="center" valign="middle"  colspan="2"  >injection</td></tr><tr><td align="center" valign="middle" >(P.)</td><td align="center" valign="middle" >(P.)</td><td align="center" valign="middle" >(P.)</td><td align="center" valign="middle"  colspan="2"  >(P.)</td></tr><tr><td align="center" valign="middle" >C1</td><td align="center" valign="middle" >0.5 &#177; 0.20</td><td align="center" valign="middle" >0.83 &#177; 0.15</td><td align="center" valign="middle" >0.49 &#177; 0.20</td><td align="center" valign="middle"  colspan="2"  >0.33 &#177; 0.19</td></tr><tr><td align="center" valign="middle" >C2</td><td align="center" valign="middle" >0.52 &#177; 0.20</td><td align="center" valign="middle" >0.86 &#177; 0.15</td><td align="center" valign="middle" >0.64 &#177; 0.19</td><td align="center" valign="middle"  colspan="2"  >0.52 &#177; 0.20</td></tr><tr><td align="center" valign="middle" >C3</td><td align="center" valign="middle" >0.61 &#177; 0.20</td><td align="center" valign="middle" >0.90 &#177; 0.12</td><td align="center" valign="middle" >0.72 &#177; 0.18</td><td align="center" valign="middle"  colspan="2"  >0.77 &#177; 0.17</td></tr><tr><td align="center" valign="middle" >C4</td><td align="center" valign="middle" >0.71 &#177; 0.18</td><td align="center" valign="middle" >1.00 &#177; 0.00</td><td align="center" valign="middle" >0.93 &#177; 0.10</td><td align="center" valign="middle"  colspan="2"  >0.81 &#177; 0.16</td></tr><tr><td align="center" valign="middle" >C5</td><td align="center" valign="middle" >0.76 &#177; 0.17</td><td align="center" valign="middle" >1.00 &#177; 0.00</td><td align="center" valign="middle" >1.00 &#177; 0.00</td><td align="center" valign="middle"  colspan="2"  >0.86 &#177; 0.14</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr></tbody></table></table-wrap><p>Data represents the mean value &#177; S.E. from 25 cotton leaf worm/group with significance difference between the five different concentrations, using Chisquare test (χ<sup>2</sup> = 47.43, d.f. = 28, P ≤ 0.01).</p><p>Different application methods of crude venom toxins on integument or into the hemolymph had not compromise the same mortality effect derived from species selectivity. Spraying and injection application of a high concentration (1 - 1.16 ml<sup>–1</sup>) of bee venom to cotton leaf worm caused significant morphological differences. However, by passing the cuticle by topical dropping and topical food applications of either social bee or wasp venom into the hemolymph (1 - 1.16 ml<sup>–1</sup> per insect) caused 100% mortality in both species within 72 h. expressing different application effects to insect pests could be remedied by applying the venom in ways that targeted the pest.</p><p>Wasp venom applied on S. littoralis has the largest effect with (χ<sup>2</sup> = 53.10; d.f. = 2; P &lt; 0.0001 for topical on food application and χ<sup>2</sup> = 12.18; d.f. = 2; P &lt; 0.002 for integument application) which is higher than bee venom mortality and toxicological effects (Figures 5(a)-(d)).</p><p>Reduced cumulative survival by bee venom spraying caused 60% for bee and 75% for wasp (F<sub>(</sub><sub>4,389)</sub> = 9.98, P ≤ 0.004) mortality for the highest concentration 0.16 while reached 75% by spraying Polistes sp. Venom compared with infection by injection that has the lowest effect for bee causing 25% mortality and 83% for wasp venoms on Spodoptera littoralis (<xref ref-type="fig" rid="fig6">Figure 6</xref> and <xref ref-type="fig" rid="fig8">Figure 8</xref>).</p><p>The mean of residual effect that calculated as the mean of cumulative mortalities from day 1 until day 5 after applying venom topically, injection and by spraying were manifested in (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="table" rid="table2">Table 2</xref>). Topical application on food and integument were detected the highest significant mortalities effect, whereas injection recorded the least significant mortality effect (18.40%) (18.40%) (F<sub>(</sub><sub>4,389)</sub> = 18.78; P &lt; 0.001)</p><p>(F<sub>(</sub><sub>4,389)</sub> = 12.46; P &lt; 0.0001) as compared to other venom application (<xref ref-type="fig" rid="fig7">Figure 7</xref>).</p><p>All treatments caused significant increases in total mortality and morphological changes during the larval until pupal stage and the sequential combined effect treatments had more decreasing effect than the individual treatments. According to the obtained result, bee and wasp venom could be considered as a biopesticide, and become more effective when used in sequential treatment (<xref ref-type="table" rid="table2">Table 2</xref> and <xref ref-type="fig" rid="fig6">Figure 6</xref>).</p><p>Furthermore, we demonstrate that, despite significant differences in their venom most venom have strikingly similar insecticidal effectiveness. The fact that similar social bee and wasp venoms are not acquiring the same mechanism of action on lepidopteran insects suggests from results that bee venom toxins have a conserved mode of action. However, the precise role of their toxins identified as social insects still remains to be determined within our study.</p></sec><sec id="s3_4"><title>3.4. Susceptibility of the Fourth Instar Larvae of Spodoptera littoralis to Different Tested Insecticides</title><p>Wasp venom applied on S. littoralis has the largest effect with (χ<sup>2</sup> = 53.10; d.f. = 2; P &lt; 0.0001 for topical on food application and χ<sup>2</sup> = 12.18; d.f. = 2; P &lt; 0.002 for integument application) which is higher than bee venom mortality and toxicological effects (<xref ref-type="fig" rid="fig7">Figure 7</xref> and <xref ref-type="fig" rid="fig8">Figure 8</xref>).</p><p>All treatments caused significant increases in total mortality and morphological changes. According to the obtained result, bee and wasp venom could be considered as a biopesticide, and become more effective when used in sequential treatment.</p></sec></sec><sec id="s4"><title>4. Discussion</title><p>The 4<sup>th</sup> instar larvae of Spodoptera littoralis were used in the current study for investigating the significant variations within the toxic biological effects of social bee and wasp venoms. The 4<sup>th</sup> instar larvae are considered as the most susceptible stage for toxic affection and when the host is at the active stage, e.g. larval/nymphal stage [<xref ref-type="bibr" rid="scirp.120343-ref28">28</xref>].</p><p>Based on LC<sub>50</sub> values, both venom compounds caused considerable toxic effects against the 4<sup>th</sup> instar larvae of Spodoptera littoralis. Wasp venom particularly had shown higher drastic toxic effects compared to bee venom toxicity. This finding agrees with [<xref ref-type="bibr" rid="scirp.120343-ref29">29</xref>] which demonstrated that honeybee venom-reactive proteins had weak cross toxic reactions compared with yellow jacket venom due to strong IgE binding significantly. This significant variation may be due to the presence of Melittin and apamin which are found in the genus Apis. However, is found in more genera, such as Vespa, Parapolybia, Protonectarina, and Polistes [<xref ref-type="bibr" rid="scirp.120343-ref30">30</xref>].</p><p>Great toxic biological effects were found to be on the development, mortality, and morphology of the larvae treated with a combination of the median lethal concentrations. Few numbers of larvae remained alive and reached the 4<sup>th</sup> larval were small size with slow motion cleared symptoms of death, while the control untreated larvae reached 6<sup>th</sup> larval stage. This may be due to the fact that venoms of both bees and wasps are being used as defensive agents against predators, competitors, and pathogens. These venoms are particularly rich in neurotoxic, cytolytic and antimicrobial peptides that fulfill key roles in capture and conservation of praise, defense against competitors [<xref ref-type="bibr" rid="scirp.120343-ref31">31</xref>] that agree with [<xref ref-type="bibr" rid="scirp.120343-ref32">32</xref>] that indicates the insecticidal activity of ectoparasitoid wasp on the cotton boll worm.</p><p>Aiming at underlying the potential of venom approaches for pharmaceutical discovery different application types for social bee and wasp venom were significantly (χ<sup>2</sup> = 239.47, d.f. = 3, P ≤ 0.0001) compared within the study. Venom application by injection had no toxic effects on larvae. However, it has the ability to cause a high malformation percentagein Spodoptera littoralis.</p><p>The concentration which causes 50% of adult mortality up to 70% resulted from the toxicity of honey bee venom components to S. littoralis larvae is due to the production of crystalline endotoxic protein. On digestion by susceptible larvae, the active toxin generated from the protoxin binds to the receptors on the gut epithelium. This leads to paralysis of gut and mouth parts causing the death of larvae [<xref ref-type="bibr" rid="scirp.120343-ref33">33</xref>]. These effects comprise destruction of epithelial cells; microvilli and the peritrophic membrane were curled and ruptured than those of control treatment. The current studies cleared the presence of liquid swelling within insect integument that can be resulted from the mixing of the gut contents with the haemolymph caused the larval mortality.</p><p>On the other hand, morphological malformations occurred to cotton worm larvae during their development may be resulted from both bee and wasp venom may be due to a potent chitin synthesis inhibitor classified as an insect growth regulator, inhibits the synthesis of chitin in larvae that have ingested it, causing the integument to become fragile, and leading to mortality during the moulting [<xref ref-type="bibr" rid="scirp.120343-ref34">34</xref>]. This finding agrees with [<xref ref-type="bibr" rid="scirp.120343-ref35">35</xref>] study on the cytotoxicity [<xref ref-type="bibr" rid="scirp.120343-ref36">36</xref>] of venom from P. hypochondriaca. Different cells of the mid-gut exhibited a swelling, appearance and microvilli showed complete disorders in many areas, increasing in goblet cells secretion with rupture of basement membrane, many vacuolations occurred in the cell cytoplasm. This can be expressed by pest response to venom injection that is often accompanied by melanization, a cascade of proteolytic reactions leading to the deposition of melanin and production of phenolic intermediates [<xref ref-type="bibr" rid="scirp.120343-ref37">37</xref>] that agree with current study results. This may occur due to the enhanced rate of absorption [<xref ref-type="bibr" rid="scirp.120343-ref38">38</xref>], the swollen and elongated protruded villi into its lumen as a bulbous version was a result of enzymatic activity of the epithelial cells [<xref ref-type="bibr" rid="scirp.120343-ref39">39</xref>]. These results are in agreement with findings of [<xref ref-type="bibr" rid="scirp.120343-ref40">40</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref41">41</xref>] and [<xref ref-type="bibr" rid="scirp.120343-ref42">42</xref>] studies on venom proteins from A. ervi [<xref ref-type="bibr" rid="scirp.120343-ref17">17</xref>] cause castration by causing apoptosis and subsequent tissue degradation [<xref ref-type="bibr" rid="scirp.120343-ref43">43</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref44">44</xref>].</p><p>Thus social bee and wasp venom may find applications as biocontrol agents against insect pests especially cotton worms that agree with [<xref ref-type="bibr" rid="scirp.120343-ref45">45</xref>]. This might explain the high malformation and mortality percentage in S. littoralis treated with social bee and wasp venoms obtained in the present work that cope with [<xref ref-type="bibr" rid="scirp.120343-ref46">46</xref>] where the venom of A. ervi induces the castration of the pea aphid Acyrthosiphon pisum. Our study findings have important implications for future applications that would aim at using crude venom or other venom bioactive proteins to efficiently control cotton worm populations.</p><p>A correlation was observed between changes in morphology and mortality of cotton worms treated with both social bee and wasp venoms. From these data, it seems that the wasp venom interferes with the activity of chitin synthesis in the cuticle in such a way that the daily rate of chitin deposition and its growth are reduced or retarded. Vinson et al. [<xref ref-type="bibr" rid="scirp.120343-ref47">47</xref>] recorded that chitin deposition was inhibited in locusts that fed on Dimilin which resulted in wrecking the cuticle and thus its rigidity was reduced to half of that of the normal cuticle. While honey bee venom interferes more with a high toxic effect on larval mortality which agree with their defence mechanism of action as bees depend on killing their insect pest than depending on their paralysis as wasps [<xref ref-type="bibr" rid="scirp.120343-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.120343-ref48">48</xref>].</p><p>Thus, strains promise to fill an important gap in current insect-management programs. This should open the way for cost-effective bio-control of a range of insect pests of agricultural and medical importance. Produce a cheap, safe, and green tool for the control of insect pests including cotton worms, which, in contrast to most chemical insecticides, will not eventually be rendered useless by the evolution of resistance.</p></sec><sec id="s5"><title>Acknowledgements</title><p>The authors extend thanks to Suez Canal University, Zoology Department, Faculty of Science as well as Plant Protection Research institute for assistance in rearing cotton worms and biochemical analysis.</p></sec><sec id="s6"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s7"><title>Cite this paper</title><p>Sadek, R.Z., El Banna, S.M., Semida, F.M. and Zalat, S.M. (2022) Potential Insecticidal Effect of a Wasp (Polistes dominulus) and a Bee (Apis mellifera) Venoms in Controlling Spodoptera littoralis. 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