REVIEW article

Front. Physiol., 25 February 2020

Sec. Invertebrate Physiology

Volume 10 - 2019 | https://doi.org/10.3389/fphys.2019.01591

A Review of Resistance Mechanisms of Synthetic Insecticides and Botanicals, Phytochemicals, and Essential Oils as Alternative Larvicidal Agents Against Mosquitoes

  • Division of Biopesticides and Environmental Toxicology, Sri Paramakalyani Centre for Excellence in Environmental Sciences, Manonmaniam Sundaranar University, Tirunelveli, India

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Abstract

Mosquitoes are a serious threat to the society, acting as vector to several dreadful diseases. Mosquito management programes profoundly depend on the routine of chemical insecticides that subsequently lead to the expansion of resistance midst the vectors, along with other problems such as environmental pollution, bio magnification, and adversely affecting the quality of public and animal health, worldwide. The worldwide risk of insect vector transmitted diseases, with their associated illness and mortality, emphasizes the need for effective mosquitocides. Hence there is an immediate necessity to develop new eco-friendly pesticides. As a result, numerous investigators have worked on the development of eco-friendly effective mosquitocidal compounds of plant origin. These products have a cumulative advantage of being cost-effective, environmentally benign, biodegradable, and safe to non-target organisms. This review aims at describing the current state of research on behavioral, physiological, and biochemical effects of plant derived compounds with larvicidal effects on mosquitoes. The mode of physiological and biochemical action of known compounds derived from various plant families as well as the potential of plant secondary metabolites, plant extracts, and also the essential oils (EO), as mosquitocidal agents are discussed. This review clearly indicates that the application of vegetal-based compounds as mosquito control proxies can serve as alternative biocontrol methods in mosquito management programes.

Introduction

Vector borne diseases account for more than seven million deaths annually (World Health Organization [WHO], 2017), among which mosquito borne diseases are the most threatening due to their wide spread occurrence, consequently featuring a higher frequency of disease transmission (Lounibos, 2002; Tyagi et al., 2015). Among different mosquito families, Culicidae is a large family (3,300 Service species-41 genera) comprising Toxorhynchitinae, Anophelinae (anophelines), and also Culicinae (culicines) sub-families (Service, 1996; Senthil-Nathan et al., 2005b). Among the 31 genera, Anopheles, Culex, and Aedes are the most detrimental. Anopheles species, are carriers of major life-threatening diseases (malaria and filariasis-transmitting agents, such as Wuchereria bancrofti, Brugia malayi, and Brugia timori) and also of a few arboviruses (Kalaivani et al., 2012; Benelli et al., 2018; Thanigaivel et al., 2019; Vasantha-Srinivasan et al., 2019).

The discovery of DDT’s insecticidal properties in late 1930s/beginning of 1940s and the following progress of organochlorine invention and organophosphate insecticides concealed biological pesticide merchandise-research since the responses to mosquito regulation were supposed to have remained established (Shaalan et al., 2005; Senthil-Nathan et al., 2006a, b). The ranges of many of the mosquito species were not limited and keep expanding, thereby up surging the rates of disease incidence. Until recently, the use of several of the earlier synthetic-insecticides, such as permethrin and malathion, along with other organophosphates in vector control programes has been partial. This is due to absence of unique-insecticides, expense of synthetic-insecticides, apprehension for ecological sustainability, damaging influence on human health, besides further non-target populations, their persistent nature, greater amount of “biological magnification” through ecosystem and also the development of insecticide resistance (Ghosh et al., 2012). The emergence of DDT resistance in Aedes species (Ae. tritaeniorhynchus and Ae. sollicitans) lead to numerous drawbacks in mosquito control programs (Brown, 1986). Several categories of Mosquitocides are being implemented in malaria control programs (BHC, organophosphorus, carbamate, and pyrethroid). The ability of mosquitoes to evade the insecticidal action of these synthetic compounds are attributed to the increase in the rate of synthesis of detoxifying enzymes such as monoxygenases (MFOs), glutathione-S-transferases (GST) and carboxyl-cholinesterase (CCE). MFOs are often associated with metabolic resistance to pyrethroids, such as permethrin, while GSTs are usually associated with organochloride resistance such as DDT. Resistance to pyrethroids, organophosphates and carbamates, such as bendiocarb are incurred by the magnification of CCE activity (Hemingway and Ranson, 2000). Added insecticides, benzylphenyl urea and the larvicide, Bacillus thuringiensis israelensis (Bti), have partial use against mosquitoes. Unpredicted natural or anthropogenic associated ecological variations that modify the original habitats severely affect the vector biology thereby positively influencing their existence and disease incidence, thus constraining the frame-work of mosquito control strategies.

Biological Management of Mosquitoes

Several phytochemicals from several plant families are identified with larvicidal activities against different mosquito species (Table 1). Plant extracts with their augmented phytochemical elements have a recognized potential as a substitute to conventional mosquito control agents (Sukumar et al., 1991; Tripathi et al., 2009; Tehri and Singh, 2015). The main strategy for mosquito control deals with the restriction of the vector population. As a promising biocontrol agent, the compounds from the plants of the family Meliaceae such as neem Azadirachta indica A. Juss (Senthil-Nathan et al., 2005b; Senthil-Nathan, 2013), Indian white cedar, Dysoxylum malabaricum Bedd. (Senthil-Nathan et al., 2006a), D. beddomei and chinaberry tree, Melia azedarach L. (Senthil-Nathan et al., 2006b) were effective against An. stephensi (Senthil-Nathan et al., 2008). “Secondary metabolites” from Eucalyptus tereticornis Sm. (forest redgum, Myrtaceae) exhibited effective mosquitocidal activities against An. stephensi as reported by Senthil-Nathan (2007). Also, the crude metabolic extracts of Acanthospermum hispidum leaves were active against An. stephensi, Ae. Aegypti, as well as Cx. quinquefasciatus as reported by Vivekanandhan et al. (2018a, b). A study conducted on testing the mosquitocidal activity of Justicia adhatoda L. (Acanthaceae) leaf extracts revealed the potential of natural larvicidal agent against Ae. Aegypti (Thanigaivel et al., 2012, 2017a,b).

TABLE 1

Family and plant speciesMajor constituentsMosquito speciesReferences
Acanthaceae
Andrographis paniculataAndrographolideAedes aegyptiEdwin et al., 2016
Alangiaceae
Alangium salvifoliumAsarinin, sesamin and (+)-xanthoxylol-γ,γ-dimethylallylether, Hexadecanoicacid,1 hydroxymethyl-1,2-ethanediyl esterAedes aegyptiThanigaivel et al., 2017a
Amaranthaceae
Chenopodium ambrosioidesα-TerpineolAedes aegyptiLeyva et al., 2009b
Amaryllidaceae
Alium macrostemonMethyl propyl disulfide; mimethyl trisulfideAedes albopictusLiu et al., 2014a
Alium monanthumDimethyl trisulfide; dimethyl tetrasulfideAedes aegyptiMoon, 2011
Anacardiaceae
Pistacia terebinthusα-Pinene; cyclopentaneCulex quinquefasciatusCetin et al., 2011
Spondias purpureaCaryophyllene oxide and α-cadinolAedes aegyptiLima et al., 2011
Annonaceae
Cananga odorataBenzyl acetate, linalool, methyl benzoateAedes aegyptiVera et al., 2014
Guatteria blepharophyllaCaryophyllene oxideAedes aegyptiAciole et al., 2011
Guatteria friesianaβ-EudesmolAedes aegyptiAciole et al., 2011
Guatteria hispidaβ-Pinene and α-pineneAedes aegyptiAciole et al., 2011
Rollinia leptopetalaSpathulenolAedes aegyptiFeitosa et al., 2009
Apiaceae
Angelica purpuraefolia4’-Chloro-4,4-dimethyl-3-(1-imidazolyl)-valerophenone, 1-Dodecanol,Aedes aegyptiNagella et al., 2012
Anethum graveolensLimonene, carvoneAedes albopictusSeo et al., 2015
Apium graveolensR-+-LimoneneAedes aegyptiPitasawat et al., 2007
Limonene, carvoneAedes albopictusSeo et al., 2015
Bupleurum fruticosumα-Pinene; β-pineneCulex pipiensEvergetis et al., 2009
Carum carviCarvoneAedes aegyptiPitasawat et al., 2007
Conopodium capillifoliumα-Pinene; sabineneAedes aegyptiEvergetis et al., 2009
Coriandrum sativumLinalool, 2,6-octadien-1-ol, 3,7- dimethyl-, acetate, E-Aedes aegyptiNagella et al., 2012
Cuminum cyminumρ-cymene, β-pinene, cuminaldehydeAedes albopictusSeo et al., 2015
Daucus carotaCarotolAedes albopictusSeo et al., 2015
Elaeoselinum asclepiumα-Pinene; sabineneAedes aegyptiEvergetis et al., 2009
Foeniculum vulgaretrans-Anethole, LimoneneAedes aegyptiRocha et al., 2015
Heracleum pastinacifoliumOctyl acetate, HexylAedes aegyptiTabanca et al., 2012a
Ligusticum chuanxiongoctadecenoic acidsAedes aegypti, Culex quinquefasciatusEvergetis et al., 2009
Oenanthe pimpinelloidesγ-Terpinene; o-cymeneAedes aegyptiPavela, 2015
Pimpinella anisumTrans-anethole, α-Pinene; sabinene, β-phellandreneAedes aegyptiPavela, 2015
Petroselinum crispumβ-phellandrene,myristicin, α & β-pinene, myrceneAnopheles culicifaciesEvergetis et al., 2012
Pe. SativumMyristicin,1,8-cineole, 1,3,8-p-menthatrieneAedes albopictusSeo et al., 2015
Trachyspermum ammiThymolAnopheles stephensiPandey et al., 2009
ρ-Cymene, γ-TerpineneAedes albopictusSeo et al., 2015
Apocynaceae
Cionura erecta L.Edren-9-one, alpha cadinol, eugenol and alpha muuroleneAnopheles stephensiMozaffari et al., 2014
Araliaceae
Dendropanax morbiferaγ-ElemeneAedes aegyptiChung et al., 2009
Aristolochiaceae
Aristolochia indicaAristolochic acid I and IIAedes aegyptiPradeepa et al., 2015
Asarum heterotropoidesMethyleugenol and safroleAedes aegyptiPerumalsamy et al., 2009
Asteraceae
Achillea millefoliumEucalyptol, β-pinene, borneol, sabinene, campheneAedes albopictusConti et al., 2010
Artemisia absinthium(Z)-β-ocimene, (E)-β-farnesene (Z)-en-yn-dicycloetherAedes aegypti, Culex quinquefasciatus, Anopheles stephensiGovindarajan and Benelli, 2016
Ar. dracunculusHexanal, isovaleric acid, (Z)-3-hexenol,Anopheles stephensiPour et al., 2016
Hexadecanol
Artemisia vulgarisCamphor, Linalool, terpenen-4-ol, a-and bthujone, b-pineneAedes aegyptiBora and Sharma, 2011
camphor, alpha-thujone, betacaryophyllene, gammamuurolene, camphene
Artemisia vulgarisMyrcene, limonene, cineolAedes aegyptiSujatha et al., 2013
Ar. NilagiricaCapillinAedes aegypti, Aedes albopictusBora and Sharma, 2011
Blumea densifloraBorneol, germacrene D, β-caryophyllene, γ-terpinene, sabinene, β-bisaboleneAnopheles anthropophagusZhu and Tian, 2011
Blumea mollisLinalool, γ-elemene, copaene, estragole, Allo-ocimene, γ-terpinene AlloaromadendreneCulex quinquefasciatusSenthilkumar et al., 2008
Chamaemelum nobileα-pineneAedes aegypti, Culex quinquefasciatusAmer and Mehlhorn, 2006
Chrysanthemum indicumverbenol, 1,8-cineole, α-pinene, camphor, borneol, bornyl acetateAedes aegyptiShunying et al., 2005
Aedes aegyptiWu et al., 2010
Eupatorium betonicaeformeβ-CaryophylleneAedes aegyptiAlbuquerque et al., 2004
Matricaria recutitaα-bisabololAedes aegyptiHeuskin et al., 2009
Pectis oligocephalap-Cymene and thymolAedes aegyptiAlbuquerque et al., 2007
Tagetes erectaPiperitoneAedes aegyptiMarques et al., 2011
Tagetes filifoliatrans-AnetholeAedes aegyptiRuiz et al., 2011
Tagetes lucidaMethyl chavicolAedes aegyptiVera et al., 2014
Tagetes minutaTrans-ocimenoneAedes aegyptiRuiz et al., 2011
Tagetes minuta5E-ocimenoneAedes aegyptiMaradufu et al., 1978
Tagetes patulaLimonene and terpAedes aegyptiDharmagadda et al., 2005
Bignoniaceae
Cybistax antisyphiliticaquinoneAedes aegyptiRodrigues et al., 2005
Boraginaceae
Auxemma glaziovianaα-Bisabolol, α-cadinol, and T-muurololAedes aegyptiCosta et al., 2004
Cordia curassavicaCordiaquinones J and KAedes aegyptiIoset et al., 2000
α-PineneAedes aegyptiSantos et al., 2006
Cordia leucomalloidesδ-Cadinene and E- caryophylleneAedes aegyptiSantos et al., 2006
Cucurbiataceae
Bryonopsis laciniosaGoniothalaminCulex pipiensKabir et al., 2003
Cupressaceae
Callitris glaucophyllaGuaiol & citronellic acidAedes aegyptiShaalan et al., 2006
Chamaecyparis formosensisMyrtenolAedes aegyptiKuo et al., 2007
Cryptomeria japonica16-Kaurene and elemolAedes aegypti, Aedes albopictusCheng et al., 2009c
Cunninghamia konishiiCedrol, α-PineneAedes aegyptiCheng et al., 2013
Cupressus arizonica var. glabraα-Pinene & epi-zonareneAedes aegyptiAli et al., 2013
Cupressus arizonicaLimonene, umbellulone α-pineneAnopheles stephensiSedaghat et al., 2011
Cupressus benthamiiLimonene; umbelluloneAedes albopictusGiatropoulos et al., 2013
Cupressus macrocarpaSabinene; α-Pinene; terpinen-4-olAedes albopictusGiatropoulos et al., 2013
Cupressus sempervirensα-Pinene; δ-3-careneAedes albopictusGiatropoulos et al., 2013
Cupressus torulosaα-Pinene; δ-3-careneAedes albopictusGiatropoulos et al., 2013
ChamaecyparisMyrtenol; myrtenalAedes aegypti, Aedes aegyptiKuo et al., 2007
formosensisLimonene; oplopanonyl acetate; beyereneAedes albopictusGiatropoulos et al., 2013
Chamaecyparis lawsonianaα-Pinene; sabinene; δ-3-careneCulex pipiensVourlioti-Arapi et al., 2012
Juniperus communis ssp.
Hemisphaericaα-Pinene; limoneneCulex pipiensVourlioti-Arapi et al., 2012
Juniperus drupaceaSabinene; 4-methyl-1-1-methylethyl-3-cyclohexen-1-olCulex pipiensVourlioti-Arapi et al., 2012
Juniperus foetidissimaMyrcene; germacrene-D; α-PineneCulex pipiensVourlioti-Arapi et al., 2012
Juniperus oxycedrus L. ssp.
oxycedrusα –pineneCulex pipiensVourlioti-Arapi et al., 2012
Juniperus oxycedrus L.
subsp. Macrocarpaα-Pinene; δ-3-carene; β-phellandrene; α-terpinyl acetateAedes albopictusGiatropoulos et al., 2013
Juniperus phoenicea
Tetraclinis articulateα-Pinene; bornyl acetateAedes albopictusGiatropoulos et al., 2013
Dioncophyllaceae
Triphyophyllum peltatumdioncophylline AAnopheles stephensiFrançois et al., 1996
Euphorbiaceae
Croton nepetaefoliusMethyleugenolAedes aegyptiMorais et al., 2006
Croton regelianusAscaridole & p-CymeneAedes aegyptiTorres et al., 2008
Croton zehntneriE-anethole, p-anisaldehydeAedes aegyptiMorais et al., 2006
Fabaceae
Copaifera multijugaβ-caryophylleneAnopheles darling, Aedes aegyptiTrindade et al., 2013
Hymenaea courbarilα-Copaene, spathulenolAedes aegyptiAguiar et al., 2010
Germacrene D and β-caryophyllene
Myroxylon pereiraeBenzyl benzoateAedes aegyptiYenesew et al., 2003
Millettia duraRotenoids, deguelin and tephrosin caryophyllene oxide; phenol,4-3,7-dimethyl-3-ethenylocta-1,6-dienyl; caryophylleneCulex quinquefasciatusDua et al., 2013
Psoralea corylifoliaCitronellolAedes aegyptiBenelli et al., 2017
GeraniaceaeCulex quinquefasciatusCavalcanti et al., 2004
Pelargonium graveolensNeral; geranialCulex quinquefasciatus
Gramineaeα-PineneAedes aegyptiCetin et al., 2011
Cymbopogon citratusThymolCulex pipiensGovindarajan et al., 2013
Hypericaceae
Hypericum scabrumΔ-3-carene, 1,8-cineole, β-caryophyllene, bicyclogermacreneCulex tritaeniorhynchus, Aedes albopictus, and Anopheles subpictusAraújo et al., 2003
Lamiaceae
Coleus aromaticusβ-caryophyllene, bergamotene, and terpinoleneAedes aegyptiJaenson et al., 2006
Hyptis martiusii
Hyptis suaveolens
Lavandula gibsoniα-Terpinolen and thymolAedes aegypti, Anopheles stephensiKulkarni et al., 2013
Culex quinquefasciatus.
Lavandula stoechasFenchone, 1,8-CineoleCulex pipiensTraboulsi et al., 2002
Lippia origanoidesCarvacrolAedes aegyptiMar et al., 2018
Mentha longifoliaPiperitenone oxidAedes aegyptiPavela et al., 2014
M. microcorphyllaPiperitenone, Pulegone, Piperitenone oxideCulex pipiensTraboulsi et al., 2002
M. spicataCarvoneAedes aegyptiGovindarajan et al., 2012
Nepeta catariaE,Z-Nepetalactone and Z, E-nepetalactoneAedes aegyptiZhu et al., 2006
Ocimum americanumE-Methyl-cinnamateAedes aegyptiCavalcanti et al., 2004
Ocimum basilicumLinalool; methyl eugenolAedes aegyptiGovindarajan et al., 2013
Ocimum gratissimumEugenolAedes aegyptiCavalcanti et al., 2004
Ocimum sanctumMethyleugenolCulex pipiensGbolade and Lockwood, 2008
O. syriacumCarvacrol, ThymolAedes aegyptiTraboulsi et al., 2002
Perilla frutescensoleic, S-limonene, perillaldehydeAedes aegyptiPohlit et al., 2011
Plectranthus amboinicusCarvacrolAedes aegyptiLima et al., 2011
Plectranthus mollisPiperitone oxide, fenchoneAedes aegyptiKulkarni et al., 2013
Pogostemon cablinPatchouli alcohol, Seyshellene, α-bulnesene, NorpatchoulenolAedes aegyptiLima-Santos et al., 2019
Pulegium vulgarePulegone; carvoneAedes albopictusPavela, 2015
Rosmarinus officinalis1,8-Cineole; camphorAedes aegyptiGiatropoulos et al., 2018
Satureja hortensisγ-Terpinene; carvacrolCulex pipiensPavela, 2009
Thymus capitatus (L.)Thymol, alpha-Amyrin, Carvacrol + beta-Mansour et al., 2000
Hoffm. & LinkCaryophylleneCulex pipiens
Thymus leucospermusp-CymeneCulex pipiensPitarokili et al., 2011
Thymus satureoidesThymol; borneolCulex pipiensPavela, 2009
Thymus teucrioidesp-Cymene; γ-terpinene; thymolAedes albopictusPitarokili et al., 2011
Thymus vulgarisa-terpinene,carvacrol, thymolGiatropoulos et al., 2018
p-cymene, linalool, geraniolAedes aegypti
Vitex agnus castusTrans-caryophyllene; 1,8 cineoleCulex quinquefasciatusNiroumand et al., 2018
Vitex trifoliaMethyl-p-hydroxybenzoateAedes aegyptiKannathasan et al., 2011
Lauraceae
Cinnamomum camphora1,8-CineoleAnopheles sinensisZhang et al., 2018
C. cassiaCinnamaldehydeAedes aegyptiZhu et al., 2006
C. impressicostatumBenzyl benzoate and α-phellandreneAedes aegyptiJantan et al., 2005
C. japonicumBorneolAnopheles sinensisZhang et al., 2018
C. microphyllumBenzyl benzoateAedes aegyptiJantan et al., 2005
C. mollissimumBenzyl benzoateAedes aegyptiJantan et al., 2005
C. osmophloeumtrans-Cinnamaldehyde and cinnamyl acetateAedes aegyptiCheng et al., 2004
C. pubescensBenzyl benzoateAedes aegyptiJantan et al., 2005
C. rhyncophyllumBenzyl benzoateAedes aegyptiJantan et al., 2005
C. scortechiniiβ-Phellandrene and linaloolAedes aegyptiJantan et al., 2005
C. sintocSafroleAedes aegyptiJantan et al., 2005
C. subaveniumEugenolAnopheles sinensisZhang et al., 2018
C. szechuanense1,8-CineoleAnopheles sinensisZhang et al., 2018
Laurus nobilis1,8-cineole, linaloolCulex pipiensPatrakar et al., 2012
Lindera obtusilobaα-Copaene; β-caryophylleneAedes aegyptiPavela, 2015
Magnoliaceae
Magnolia salicifoliaTrans-anethole, Methyl eugenol, isomethyl eugenol, Costunolide, lactone and parthenolideAedes aegyptiKelm et al., 1997
Malvaceae
Abutilon indicumβ-sitosterolAedes aegypti,Rahuman et al., 2008a
Azadirachtin, salannin, deacetylgedunin, gedunin, 17-hydroxyazadiradione and deaceytlnimbin
Meliaceae
Azadirachta indicaSaponinsAnopheles stephensi,Senthil-Nathan et al., 2005a
23-O-methylnimocinolide
6α-O-acetyl-7-deacetylnimocinolCulex quinquefasciatusAnsari et al., 2005
Nimocinolide; 7-O-deacetyl-23-O-methyl-Aedes aegyptiSiddiqui et al., 1999
7α-O-senecioylnimocinolideBanerji and Nigam, 1984
desfurano-6α-hydroxyazadiradioneNaqvi, 1987
22,23-dihydronimocinolAedes aegyptiSiddiqui et al., 2002
1α-acetyl-3α-propionylvilasininAedes aegyptiSiddiqui et al., 2003
MeliatetraolenoneAedes aegyptiSiddiqui et al., 2003
azadirachtin, salannin, deacetylgedunin,Culex quinquefasciatusSiddiqui et al., 2003
gedunin, 17- hydroxyazadiradione
deacetylnimbinAnopheles stephensiSenthil-Nathan et al., 2005a
3β,24,25-trihydroxycycloartaneAnopheles stephensi
Dysoxylum malabaricumBeddomei lactoneAedes aegyptiSenthil-Nathan et al., 2009
D. beddomeiCaryophyllene epoxideAedes aegyptiSenthil-Nathan et al., 2009
cis-Caryophyllene
Guarea humaitensis1α,7α,11β-triacetoxy-4α-carbomethoxy-Aedes aegyptiMagalhães et al., 2010
G. scabra12α-(2-methylpropanoyloxy)-14β,15β-epoxyhavanensinAedes aegyptiMagalhães et al., 2010
Turraea floribunda1α,11β-diacetoxy-4α-carbomethoxy-7α-Aedes aegyptiNdung’u et al., 2004
hydroxy-12α-(2-methylpropanoyloxy)-15-Aedes aegyptiNdung’u et al., 2004
oxohavanensin; 1α-acetyl-3α-Culex pipiensNdung’u et al., 2004
propionylvilasininCulex pipiensNdung’u et al., 2003
Turraea wakefieldii11β,12α-diacetoxyneotecleaninCulex pipiensNdung’u et al., 2003
11β,12α-diacetoxy-14β,15β-Aedes aegyptiNdung’u et al., 2003
epoxyneotecleaninAedes aegyptiNdung’u et al., 2003
Myrtaceae
Eucalyptus benthamiiα-PineneAedes aegyptiLucia et al., 2012
E. botryoidesp-Cymene, α-eudesmol, and 1,8-cineolAedes aegyptiLucia et al., 2012
E. camaldulensis1,8-Cineol, p-cymene and β-phellandreneAedes aegyptiLucia et al., 2008
E. citriodoraCitronellal; citronellol;Aedes aegyptiVera et al., 2014
α-humulene isopulegol
E. dunnii1,8-Cineol and γ-terpineneAedes aegyptiLucia et al., 2008
E. fastigatap-CymeneAedes aegyptiLucia et al., 2012
E. globulus1,8-CineolAedes aegypti Anopheles arabiensisMassebo et al., 2009
E. grandisα-PineneAedes aegyptiLucia et al., 2007
E. gunnii1,8-Cineol and p-cymeneAedes aegyptiLucia et al., 2008
E. nobilis1,8-CineolAedes aegyptiLucia et al., 2012
E. radiata1,8-CineolAedes aegyptiLucia et al., 2012
E. robustaα-PineneAedes aegyptiLucia et al., 2012
E. saligna1,8-Cineol and p-cymeneAedes aegyptiLucia et al., 2008
E. tereticornisβ-Phellandrene and 1,8-cineolAedes aegyptiLucia et al., 2008
E. urophylla1,8-CineolAedes aegyptiCheng et al., 2009b
E. melanadenia1,8-CineolAedes aegyptiAguilera et al., 2003
Myrtus communis1,8 Cineole, α-Pinene, LinaloolCulex quinquefasciatusTraboulsi et al., 2002
M. dissitifloraTerpinen-4-olAedes aegyptiPark et al., 2011
M. leucadendron1,8-Cineol, α-pinene, and α-terpineolAedes aegyptiLeyva et al., 2008
M. linariifoliaTerpinem-4-ol and γ-terpineneAedes aegyptiPark et al., 2011
M. quinquenervia1,8-Cineol and E-nerolidolAedes aegyptiPark et al., 2011
Pimenta dioicaEugenol, linaloolAedes aegyptiPereira et al., 2014
P. racemosaTerpinem-4-ol and 1,8-cineolAedes aegyptiAciole, 2009
P. guajava1,8-Cineol and β-caryophylleneCulex pipiensLeyva et al., 2009a
1,8-CineolAedes aegyptiLima et al., 2011
P. rotundatumEugenolAedes aegyptiAguilera et al., 2003
Syzygium aromaticumEugenolAedes aegyptiCosta et al., 2005
Orchidaceae
Vanilla fragrans4-ethoxymethylphenol, 4-butoxymethylphenol, vanillin, 4-hydroxy-2-methoxycinnamaldehyde and 3,4-dihydroxyphenylacetic acidCulex pipiensSun et al., 2001
Pinaceae
Cupressus L.,limonene, α & β-pinene,Aedes aegyptiBurfield, 2000
Juniperus L.3-careneAedes aegyptiBurfield, 2000
Pinus brutiaα-Pinene and β-pineneAedes albopictusKoutsaviti et al., 2015
P. halepensisβ-CaryophylleneAedes albopictusKoutsaviti et al., 2015
P. kesiyaα-Pinene, β-pinene, myrcene and germacrene D.Aedes aegypti, Culex quinquefasciatus,Govindarajan et al., 2016
Anopheles stephensi
P. longifoliak-terpineolCulex quinquefasciatus, AnophelesAnsari et al., 2005
culicifacies
P. stankewicziiGermacrene D α-Pinene and β-pineneAedes albopictusKoutsaviti et al., 2015
P. sylvestrisEugenol 3, Cyclohexene-1-methanol, α-4-Aedes aegypti, Culex quinquefasciatusFayemiwo et al., 2014
trimethyl
Piperaceae
Piper auritum
P. betle
P. capense
P. decurrens
Safrole
Citronellal
2,3-Dihydro-2-(4′-hydroxyphenyl)-3-methyl-5(E)-propenylbenzofuran (conocarpan), 2-(4′-hydroxy-3′-methoxyphenyl)-3-methyl-5(E)-propenylbenzofuran (eupomatenoid-5), 2-(4′-hydroxyphenyl)-3-methyl-5(E)-propenylbenzofuran (eupomatenoid-6), 2,3-dihydro-5-formyl-2-(4′-hydroxyphenyl)-3-methylbenzofuran (decurrenal), and 3,7,11,15-tetramethyl-2(E)-hexadecen-1-ol (trans-phytol)
Aedes aegypti
Aedes aegypti
Aedes atropalpus
Aedes aegypti
Leyva et al., 2009b
Wahyuni, 2012
Chauret et al., 1996
de Morais et al., 2007
P. gaudichaudianumCaryophyllene oxide, β-selineneAedes aegyptide Morais et al., 2007
P. hostmanianumAsaricin and myristicinAedes aegyptide Morais et al., 2007
P. humaytanumβ-selinene, caryophyllene oxideAedes aegyptide Morais et al., 2007
P. klotzschianum1-Butyl-3,4-methylenedioxybenzene,Aedes aegyptido Nascimento et al., 2013
P. longumlimonene, and α-phellandreneCulex pipiensLee, 2000
PipernonalineAedes aegyptiYang et al., 2002
Aedes aegyptiCosta et al., 2004
P. marginatumIsoelemecin, apioleAedes aegyptiAutran et al., 2009
(Z)-AsaroneAedes aegyptiAutran et al., 2009
P. permucronatum(E)-Asarone, patchouli alcoholAedes aegyptide Morais et al., 2007
Dillapiole and myristicin
Plumbaginaceae
Plumbago zeylanicaPlumbaginAedes aegyptiPradeepa et al., 2016
Poaceae
Cymbopogon citratusGeranialAedes aegyptiCavalcanti et al., 2004
Cymbopogon flexuosuscitral a-pineneAedes aegyptiSyed and Leal, 2008
Cymbopogon nardusGeranial; neralAedes aegyptiVera et al., 2014
GirgensohnineAedes aegyptiCarreño-Otero et al., 2018
Vetiveria zizanioidesCitronellalAedes aegyptiFradin and Day, 2002
khusimol, isonootkatool, β-vetivenene, α &Aedes aegyptiVera et al., 2014
β-vetivones
Papilonaceae
Neorautanenia mitisNeotenone, neorautanone, pterocarpans neoduline, nepseudin,4-methoxyneodulineCulex quinquefasciatus, Anopheles gambiaeJoseph et al., 2004
Aedes aegypti, Aedes albopictus
Elemol, EudesmolsCulex quinquefasciatusZhu et al., 2006
Rutaceae
Chloroxylon swieteniaHeptacosanoic acidAedes aegypti, Culex quinquefasciatusBalasubramani et al., 2015
Citrus aurantifoliaGeijerene, Limonene, Germacrene DAedes aegypti, Anopheles stephensiKiran et al., 2006
Citrus hystrixα-terpineol
Citrus limonβ-Pinene; d-limonene; terpinene-4-olCulex pipiensSutthanont et al., 2010
LimoneneAedes aegypti
Citrus reticulataD-Limonene; γ-terpineneCulex quinquefasciatusMichaelakis et al., 2009
Citrus sinensisLimoneneAedes aegyptiSutthanont et al., 2010
Limonin, Nomilin, ObacunoneCulex quinquefasciatusJayaprakasha et al., 1997
Geijerene; limonene; germacrene DAedes aegyptiVera et al., 2014
Chloroxylon swietenia
Kiran et al., 2006
Clausena excavateSafrole and terpinoleneAedes aegypti, Aedes albopictusCheng et al., 2009a
Feronia limoniaEstragole and β-pineneAedes aegyptiSenthilkumar et al., 2013
F. limonian-hexadecanoic acidCulex quinquefasciatusRahuman et al., 2000
Ruta graveolensUndecan-2-oneAedes aegyptiTabanca et al., 2012b
Swinglea glutinosaβ-Pinene; piperitenone;Aedes aegyptiVera et al., 2014
α-Pinene
Toddalia asiaticaLinaloolAedes aegyptiNyahanga et al., 2010
Zanthoxylum armatumLinaloolAedes aegyptiTiwary et al., 2007
Z. articulatumViridiflorolAedes aegyptiFeitosa et al., 2007
Z. avicennae1,8-CineoleAedes albopictusLiu et al., 2014b
LimoneneAedes aegyptiPitasawat et al., 2007
Methyl heptyl ketoneAedes aegyptiBorah et al., 2012
Z. piperitumAsarinin, sesamin and (+)-xanthoxylol-γ,γ-dimethylallyletherAedes aegypti, Culex pipiensKim and Ahn, 2017
Z. monophyllumGermacrene D-4-ol and a-CadinolAedes albopictus, Culex quinquefasciatus, Anopheles stephensiPavela and Govindarajan, 2017
Santalaceae
Santalum L. spp.α-santalolAedes aegypti, Culex pipiensJones et al., 2007
Santalum albumGuaiol, elemol, and eudesmolAnopheles stephensi,Amer and Mehlhorn, 2006
SchisandraceaeAedes aegypti
Illicium verumEugenol, α-Terpinyl acetate, Eucalypt, ol, (E)-anetholeCulex quinquefasciatusKimbaris et al., 2012
Scrophulariaceae
Capraria biflora L.α-HumuleneAedes aegyptiSouza et al., 2012
Stemodia maritimaβ-Caryophyllene and caryophyllene oxideAedes aegyptiArriaga et al., 2007
Tiliaceae
Microcos paniculataN-Methyl-6b-(deca-l’,3’,5’-trienyl)-3b-methoxy-2bmethylpiperidineAedes aegyptiBandara et al., 2000
Verbenaceae
Duranta repensβ-amyrin and 12-oleanene 3β, 21β-diol,Culex quinquefasciatusNikkon et al., 2010
Lantana camaraBicyclogermacrene and E-caryophylleneAedes aegyptiCosta et al., 2010
Eucalyptol, caryophyllene,
Lippia albaCarvone; limoneneAedes aegyptiSantiago et al., 2006
L. gracilisCarvacrolAedes aegyptiSantiago et al., 2006
L. origanoidesCarvacrol; p-cymeneAedes aegyptiVera et al., 2014
L. javanicaAllopurinol,camphor, Limonene, a –terpeneol, verbenoneAedes aegyptiMwangi et al., 1992
L. microphylla1,8-cineole, thymol, α-pineneAedes aegyptiSantiago et al., 2006
L. nodifloraCamphor, p-cymene, γ−terpineneAedes aegyptiSantiago et al., 2006
L. sidoidesThymolAedes aegyptiCosta et al., 2005
Zingiberaceae
Alpinia purpurataβ-Caryophyllene and β-pineneAedes aegyptiSantos et al., 2012
Curcuma aromatic1H-3a,7-Methanoazulene and curcumeneAedes aegyptiChoochote et al., 2005
Turmerone, curcumene, and zingiberene
Curcuma longa1,8-Cineol and p-cymeneAedes aegyptiLeyva et al., 2008
Curcuma zedoariaDodecanalAedes aegyptiPitasawat et al., 2007
Hedychium coccineum1,8-Cineol and β-pineneAedes aegyptiSakhanokho et al., 2013
Hedychium sp.1,8-CineolAedes aegyptiSakhanokho et al., 2013
Kaempferia galangaEthyl trans-p-methoxycinnamateAedes aegyptiMunda et al., 2018
Kaempferia galangaEthyl cinnamateAedes aegyptiMunda et al., 2018
Zingiber officinale4-GingeroAedes aegypti, Culex quinquefasciatusRahuman et al., 2008b
Zingiber officinale6-DehydrogingerdioneAedes aegypti, Culex quinquefasciatusRahuman et al., 2008b
Zingiber officinale6-DihydrogingerdioneAedes aegypti, Culex quinquefasciatusRahuman et al., 2008b
Zingiber zerumbetα-Humulene; zerumboneAedes aegyptiSutthanont et al., 2010

Phytochemicals identified from the specific plant families and their larvicidal activity on the mosquito species.

Besides secondary metabolites, essential oils (EOs) from plants were also recorded with effective mosquitocidal potentials. The EOs from the plants of Lamiaceae and Zingiberaceae were proved with bioactivity against Ae. aegypti (Kalaivani et al., 2012). The fern Actiniopteris radiata was testified with novel mosquitocidal activity against larvae of Ae. aegypti and An. Stephensi (Kamaraj et al., 2018). The seed oil extract of Acacia nilotica possessed robust larvicidal action against major mosquito vectors (Vivekanandhan et al., 2018a). A remarkable biological activity of EOs against Dengue vectors has been extensively reviewed by Chellappandian et al. (2017, 2018, 2019). Plant volatile oils were also conveyed with mosquitocidal potentials. As studied by Vasantha-Srinivasan et al. (2018), the crude volatile oil (CVO) from Piper beetle leaves possessed significant larvicidal, ovipositional, and repellency effects against Ae. Aegypti.

Derivatives of plants are enriched with active molecules with exceptional mosquitocidal properties and can be advanced as low cost environmentally friendly bio-pesticides. Many botanical extracts along with their chief constituents showed effective insect metabolism inhibition or stimulation of digestive enzymes (Senthil-Nathan et al., 2009; Napoleão et al., 2012; Senthil-Nathan, 2013). Unlike synthetic chemicals, previous literature on plant compounds doesn’t provide any indication for the emergence of resistance so far. This is most likely due to the blend of several bioactive compounds with different mechanisms of action and therefore it is difficult for mosquito vectors to develop resistance (Mulla and Su, 1999; Shaalan et al., 2005).

Impact of Phytochemicals on the Physiology of Mosquito Larvae

As in general, plant secondary metabolites are evolved as protection mechanism against herbivory. When these toxic substances are encountered by the mosquitoes, a relatively unambiguous response is triggered that has a non-specific influence on a wide range of molecular targets such as proteins, nucleic-acids, bio-membranes, besides added cellular components. Consequently, the physiology is disrupted at numerous receptor sites, eventually causing an abnormality in the nervous system. Plant metabolites affect several vital physiological functions that include inhibition of “AChE” as well as “GABA-gated” chloride channel, disruption of Na–K ion exchange besides constricting the cellular respiration. As a subsequent event, the alteration of these enzyme levels gives rise to several anomalies that include the obstruction of nerve cell membranes and octopamine receptors along with calcium channel blockage, resulting in hormonal imbalance, mitotic poisoning, and also modifications of the molecular basis of morphogenesis (Rattan, 2010).

Synthetic insecticides generally increase the level of detoxifying enzymes. Phytochemicals target the mentioned cellular mechanisms and potentially disturb their functions (Figure 1; Zibaee and Bandani, 2010; Zibaee, 2011; Kaur et al., 2014; Senthil-Nathan, 2015). Physiological effects of phytochemicals are discussed below.

FIGURE 1

Impact of Phytochemicals on Detoxifying Enzymes

The antioxidant and detoxification enzymes of mosquito vectors are vital in detoxification of reactive oxygen species (ROS) synthesized by the toxic chemicals (Rattan, 2010). Esterase and phosphatase of the mosquito vectors plays a key role in several physiological events (Koodalingam et al., 2014). Excessive usage of toxic chemicals on mosquito control caused insecticide resistance through sodium channel mutations, activation of detoxification enzymes, and upregulation of key genes and other regulatory components like MicroRNAs (miRNAs). The CYP450s, GSTs, SOD, and esterase gene families are recognized as the foremost four enzymes accountable for the metabolic-resistance of the insects (Hemingway et al., 2004). Generally, detoxifying enzymes are involved in digestion, reproduction, juvenile hormone metabolism, neuronal conduction, moulting, and more importantly detoxification of toxic chemicals (Koodalingam et al., 2014). Phosphatases are involved in tissue development, cellular differentiation, carbohydrate metabolisms, and synthesis of ATP (Koodalingam et al., 2014). Mainly these two major classes of detoxifying enzymes are considered for evaluating the impact of toxic chemicals on physiological or biochemical events of arthropod vectors.

Carboxyl-esterases (EC3.1.1.1) are non-specific omnipresent enzymes that are associated to the major “endogenous” functions in insects, which hydrolyze a different carboxylic-acid ester (Lija-Escaline et al., 2015). Generally, the metabolic pathway of these enzymes was targeted by the chemical pesticides, especially the fourth generation class of Pyrethroids, which acts on the voltage sensitive sodium channels and blocks the mosquito nervous system (Hong et al., 2014). Esterases can also target by sequestering the insecticide through rapid binding and slowly releasing the insecticide metabolites (Karunaratne et al., 1993). This latter type of resistance requires the presence of increased quantities of esterase due to the 1:1 stoichiometry of the reaction and decreases the metabolic breakdown time.

Plant extracts and their derivatives have been widely reported to decrease the levels of carboxylesterase (α- β-carboxylesterase) level in the Ae. aegypti larva (Koodalingam et al., 2014; Lija-Escaline et al., 2015). Besides exhibiting larvicidal activity Alangium salvifolium, also substantially reduced the levels of α, β-carboxylesterase as well as superoxide dismutase (SOD) in Ae. Aegypti (Thanigaivel et al., 2017a). Myrrh commiphora molmol (oil and oleo-resin extract) instigated biochemical changes in Cx. pipiens that affected the cell proteins, as well as loss of enzyme activity (Massoud et al., 2001).

Higher rates of enzyme activities, such as SOD (Agra-Neto et al., 2014; Lija-Escaline et al., 2015) and physiological enzymes like esterase (Wheelock et al., 2005; Lija-Escaline et al., 2015), phosphatases (Walter and Schütt, 1974; Urich, 1994) are recorded with increasing developmental stages and these are considered responsible for increased pyrethroid resistance. The Mosquito vectors that established resistance to Temephos have been found to possess genes that insensitized ACHE on exposure to pesticides. Insects were also characterized by the over expression of varied forms of detoxifying enzymes (GST, SOD, and esterases) (Larson et al., 2010).

Glutathione-S-transferases are a class of detoxification enzymes considered to play a vital role in the existence of insects exposed to toxic metabolites. Increased GST activities are connected with the expression of metabolic resistance toward insecticides (Clark, 1990). GSTs can break down a broad range of substances; amplified GST activity is possibly as a response to an environmental stress. Generally, Cytochrome P450s (CYP450) displayed upregulation when induced by plant secondary metabolites in diverse insect pests especially against the vectors of human diseases (Caballero et al., 2008) and have members which are considered as major elements conferring resistance against insecticides (i.e., CYP2, CYP4, and CYP6) (Sun et al., 2001). The upregulation of GST enzymes usually at the exposure of a prominent dosage of plant compounds suggests the activity of a major detoxification process (Edwin et al., 2016). Consequently, the levels of GST expression may be used as a biomarker to detect the development of resistance (Jukic et al., 2007).

CYP450 group of enzyme family are also designated as key indicators of metabolic resistance besides susceptibility to insecticides (David et al., 2013). Many previous research outcomes proved alteration or inhibition in the expression of major detoxifying enzymes exposed to plant chemicals. Thanigaivel et al. (2017a) showed increase in the rate of GST activity in IV instar larvae of dengue mosquito exposed to methanolic leaf extract of J. adhatoda with their major derivative 3-hydroxy-2,3-dihydropyrrolo[2,1-b]quinazolin-9(1h) one (26.37%). Likewise, carboxylesterase activities differed significantly in Ae. aegypti post treatment with the leaf extracts of P. nigrum with their major derivatives thymol (20.77%) (Lija-Escaline et al., 2015). Correspondingly, the activity of major enzymes (esterases, GST, and CYP450) of dengue mosquito severely affected post treated with dynamic plant compound andrographolide derived from Andrographis paniculata (Acanthaceae) at the maximum dosage of 12 ppm (Edwin et al., 2016). DDT resistance in the mosquito An. gambiae is correlated elevated glutathione transferase (GST) E2 activity (AgGSTE2) (Enayati et al., 2005). The DDT resistant An. gambiae evades the insecticidal activity by the dehydrochlorination of DDT to its non-insecticidal metabolite DDE. Muleya et al. (2008) reported that compounds -epiphyllocoumarin (Tral-1), knipholone anthrone, isofuranonaphthoquinones (Mr 13/2, Mr13/4), and the polyprenylated benzophenone (GG1) were potent inhibitors of AgGSTE2.

Besides the botanical extracts, EO derived from the plants also have strong inhibition of detoxifying enzymes of arthropod vectors (Pavela, 2015). EOs may provide substitute sources of vector control since they are enriched with diverse phyto-molecules with insecticidal properties (Cheng et al., 2013). Insecticide phytochemicals from EOs belong to terpenoids chiefly and Phenylpropanoids to a limited extent. In which, Terpenoids includes monoterpenes and sesquiterpenes as the major compositions of EOs (Chellappandian et al., 2018). Lee et al. (2003) specified that volatile and lipophilic monoterpenoids infiltrate insect body, where they afflict physiological processes, and hence their mode of action is hard to elucidate. Previous research of Vasantha-Srinivasan et al. (2017) showed that the CVO derived from Piper betle (L.) (Pb-CVO) showed upregulation in the level GST and CYP450 and down regulate the expression of Carboxylesterases activity against the field and laboratory strains of Ae. aegypti. Moreover, the above results also showed that the changes in the level of enzymes are steady in both field and laboratory strains compared to the chemical pesticides. Due to enriched chemical diversity and potential mosquitocidal activity, CVO have acquired greater interest from researchers looking for new besides natural replacements to chemical-pesticides in controlling medically challenging pests (Pavela, 2015). Correspondingly, EO constituent’s nootkatone and carvacrol from Alaskan yellow cedar tree inhibits 50% of acetylcholine esterase activity in Ae. aegypti compared to the carbaryl, a known acetylcholinesterase inhibitor (Anderson and Coats, 2012). The impact of major plant molecules against the mosquito larvicides was tabulated (Table 1). Hence, expression of these molecules on detoxifying and metabolic enzymes is considered an important biomarker to evaluate the mosquitocidal potential of bio-rational plant metabolites.

Pradeepa et al. (2014) have reported the antimalarial activities from the compound plumbagin, identified from the rhizome of Plumbago zeylanica against An. stephensi. Also, it was revealed that plumbagin constrains the vector AchE enzyme, An. Stephensi in a dose dependent manner and also can be considered for controlling resistant vectors whose insecticide resistance is associated to an increased SOD activity (Pradeepa et al., 2016). The detection of SOD activity in the anal gills of An. stephensi larvae could be associated with their resistance provided against damaging oxygen products (Nivsarkar et al., 1991). The sensitivity of an insect to an insecticide can hence be increased by identifying certain compounds that can deactivate these enzymes (Larson et al., 2010).

Impact of Phytochemicals on Midgut Tissues

The midgut of the mosquito larvae is the chief interface of exterior environment and chip in major process like digestion, ion transport, absorption, and osmoregulation process (Bernick et al., 2008; Elumalai et al., 2016). Generally, gut region is the target of numerous insecticidal complexes and its integrity is dynamic for digestion and conferring of resistance against toxins (Stenfors Arnesen et al., 2008). With the insect midgut being the important site for synthesis of digestive enzymes, plant derived molecules primarily targets thee gut epithelium layer (EL) (Senthil-Nathan et al., 2008). This might be the significant cause for condensed metabolic rate in addition to a reduced enzyme activity (Selin-Rani et al., 2016). The peritrophic membrane (pM) gaurds the EL from the surrounding the gut lumen (GL) (Lija-Escaline et al., 2015). Phyto-chemicals are proven to exert a serious impact on the digestive epithelial cells and further decrease the growth rate of arthropods (Yu et al., 2015). Neira-Oviedo et al. (2008) stated that plant compounds flow into the gastric caeca and the malpighian tubules thereby affecting the midgut epithelium. For instance, extracts of M. azedarach have been reported to cause extensive harm on the EL and pM of filarial vector Cx. quinquefasciatus (Al-Mehmadi and Al-Khalaf, 2010). The pM may influence the growth and development of parasites vectors by creating a mechanical barrier to invasion by ookinetes (Rudin and Hecker, 1989). Plant extracts and their metabolites are crucial for the impairment of pest mid-gut epithelium (Rey et al., 1999). The compound catechin isolated from Leucas aspera affects the mid-gut of the three mosquito larvae Ae. aegypti, An. stephensi, and Cx. quinquefasciatus (Elumalai et al., 2016). Previous photomicrographic study on the midgut tissues of the dengue mosquito (Field and laboratory strains of Ae. aegypti) treated with the CVO of P. betle displayed severe injuries to the GL and EL (Vasantha-Srinivasan et al., 2018). Correspondingly, leaf extracts of Aristolochia indica L. (Aristolochiaceae) and their derivatives aristolochic acid I and II showed severe damage on the midgut vacuolated gut epithelial columnar cells (epi), GL, and pM (Pradeepa et al., 2015). Likewise, methanolic leaf extracts of P. nigrum severely affected the midgut cellular organelles of Ae. aegypti at the minimal dosage of 10 ppm (Lija-Escaline et al., 2015). Similarly, Vasantha-Srinivasan et al. (2018) reported that P. betle CVO derived from P. betle at the sub-lethal dosage damage the pM, and major alteration in the alignment of EL and GL of dengue mosquito comparable to the control. Previous research on Andrographolide a major derivative of A. paniculata against dengue mosquito gut cells proved that there was an unembellished collapse in the mid-gut pM, in addition to a chief variation in the El and GL alignment (Edwin et al., 2016). Selin-Rani et al. (2016) reported that the active plant molecules may damage the gut epithelium is the vital reason for concentrated metabolic rate and decrease in the enzyme-activity. Midgut cell damage is directly linked to the digestive and detoxifying enzymes dysregulation (Senthil-Nathan et al., 2008). This was also confirmed by histological studies of the mosquitoes that displayed midgut cell damage, post treatment with various botanical compounds (Yu et al., 2015). Further, treatment with plant compounds were also associated with altered protein (Fallatah, 2014) and biochemical profiles in mosquitoes (Senthilkumar et al., 2013).

Biochemical studies on Cx. pipipens exposed to Allium satvium, Citrus limon, and Bti were observed by Saeed et al. (2010). Results revealed that the use of plant oil extracts and Bti have great effect on total protein content of treated mosquito larvae. Fallatah (2010) reported the effect of water extract of fenugreek have high larvicidal effect against Cx. quinquefasciatus, causing noticeable effects on numerous body tissues together with the midgut and nervous system as well as total protein content. Aristolochic acids isolated from A. indica Linn, mainly affected the midgut EL and secondly the larval muscles and cells (Pradeepa et al., 2015). Similar results were also observed in mosquitoes treated with plant extracts (Costa et al., 2012). The orientation of the cytoplasmic protrusions of the apical surfaces of columnar cells toward the lumen suggests the secretion of apocrine and/or apoptosis.

Al-Mekhlafi (2018) reported the effect of Arum copticum (Apiaceae) extract against Culex pipiens larvae. Apart from exhibiting larvicidal activity, the extract was able to display cytopathological alterations of the midgut epithelium. EO and enriched fraction of Peumus boldus displayed larvicidal activity against Cu. Quinquefasciatus. The treated larvae displayed morphological changes in the midgut cells (de Castro et al., 2016). Velu et al. (2015) tested the peel extract of A. hypogaea against Aedes aegypti and Anopheles stephensi. The histopathological studies exposed midgut tissue damage and cuticle injury. Costa et al. (2012) reported similar aberrations in Ae. aegypti larvae (III instar) treated with Annona coriacea extract. Ae. aegypti larvae exposed to squamocin from Annona mucosa Jacq. (Annonaceae) displayed larvicidal and cytotoxic action with changes in the midgut epithelium and digestive cells by increasing the expression of autophagy genes (Costa et al., 2014, 2017). da Silva Costa et al. (2018) also reported that squamocin affected the osmoregulation and ion-regulation of Ae. aegypti larvae which resulted in a lethal effect caused by the development of a great vacuolization in the anal papillae wall.

The histopathological study of Ae. aegypti treated with methanol extract derived from seaweeds Sargassum binderi showed that larvae treated with seaweed extracts had cytopathological alteration of the midgut epithelium. The morphological observation revealed that the anal papillae and terminal spiracles of larvae were the common sites of aberrations (Yu et al., 2015). Phytochemicals (oleic, linoleic, linolenic, palmitic, and stearic acids) and their respective methyl esters were tested against fourth instar Cu. quinquefasciatus larvae. The compounds were found to affect its metabolism and the morphology of midgut along with their fat body (de Melo et al., 2018).

Impact of Phytochemicals on the Insect Behavior

With the development of resistance by this time attained to almost all available chemicals, strategies integrating “plant derived” compounds to influence “semiochemical”-mediated behaviors by means of interruption of mosquito-olfactory sensory system have substantially developed (Muema et al., 2017). As a consequence, the physiological status related to the olfactory sensory system is disrupted. The phytochemicals will bind to these odorant chemoreceptors and subsequent flight orientations of the mosquitoes are hindered (Bohbot et al., 2010). Henceforth the physiological status for instance “circadian-regulated appetitive stimulus” or “gonotrophic status” that triggers olfaction in pursuit of nutritious sources, mates and oviposition sites are disturbed. Plant-based semiochemicals can be exploited to lure the mosquitoes to an insecticide trap, thereby forming an integral part of an integrated vector control programe (Kamala-Jayanthi et al., 2015). Rice volatiles on evaluation with BioGent (BG) sentinel traps elicited antennal responses that stimulated long range oviposition site seeking behavior. Also, p-cresol, from Bermuda grass hay infusion was reported with avoidance response to gravid An. Gambiae (Eneh et al., 2016).

Future Perspectives

Higher rates of anthropogenic activities that are expected to expand with the population increase will increase the incidence of vector borne diseases. Additionally, the development of resistance among the vector population against the synthetic chemical insecticides along with their persistence in the environment and toxicity for non-target organisms are reducing the efficiencies of vector management practices globally. Hence novel plant-based compounds that are safe and effective are being focused for the development of improved management of vectors.

The research has now moved on from the isolation of bioactive compounds with anti-vector potentials to formulate novel application methods. Apart from the direct application of plant metabolites in vector control, nanoparticles (NPs) synthesized from plants using green technology are emerging as a new trend. Nanotechnology is presently “revolutionizing” the manufacture of commercial pesticides. Production of green NPs and nanoencapsulation compounds upsurges the permanence of EOs through “slow-release” phenomenon deliberating sustained fortification against mosquito bites. As reported by Jinu et al. (2018), silver nanoparticles (AgNPs) from Cleistanthus collinus Karra and Strychnos nux-vomica Linn nux-vomica presented highest larvicidal activity against A. stephensi and A. aegypti. Murugan et al. (2018a, b) proved the efficacy of zinc oxide NPs fabricated using the brown macroalga Sargassum wightii Greville ex J. Agardh. against An. stephensi. In another study reported by Murugan et al. (2018b), Poly (Styrene Sulfonate)/Poly (allylamine hydrochloride) encapsulation of TiO2 NPs were found to enhance their toxicity against mosquito vectors of Zika virus.

Conclusion

Mosquito vector borne diseases are a major human health problem in all countries. There has been an alteration toward plant-based insecticides to overcome the problems related with the use of synthetic mixtures in mosquito control programe. Botanicals can be used as mosquitocides for killing both larvae and adult mosquitoes. However, only very few botanicals have moved from laboratory to the field use, which may be due to the light and heat variability of phytochemicals compared to synthetic insecticides. Further these botanicals have been widely explored, but only a comparatively small number of patents have been filed with the persistence of regulating the formulations for use against mosquito species in the field level.

Although the activity of phytochemicals are generally attributed to some specific compounds, but there is increasing evidence that the combination of botanicals and biopesticides will result in an increased bioactivity compared to single phytochemicals (Senthil-Nathan et al., 2005a; Senthil-Nathan and Kalaivani, 2005, 2006).

At present, botanical insecticides make <1% of the world’s pesticide market (Sola et al., 2014). Isolation of active principles and synthesis of secondary metabolites of botanicals against mosquito threat are very important for the management of vector borne diseases. The positive results of initial studies on larvicidal potential of botanicals encourage further interest to investigate the bioactive compounds. Identifying botanical insecticides that are effective as well as appropriate and adaptive to overcome ecological hazards, biodegradable, and have a broad spectrum of larvicidal properties will work as a new defense in the arsenal of insecticides and it may act as an appropriate alternative product to fight against vector-borne diseases.

Thus, the present review collects important information on plant extracts along with their active molecules as agents affecting the physiology and behavior of medically threatening mosquito vectors. Now collective efforts are needed to take advantage of the accumulated knowledge on phytochemical action on mosquitos in order to integrate their application in integrated pest management programs.

Statements

Author contributions

SS-N collected all the information and wrote the review.

Acknowledgments

I am very grateful to Dr. Sylvia Anton for her thorough and constructive review and suggestion on the first draft of the manuscript.

Conflict of interest

The author declares that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

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Summary

Keywords

biopesticide, vector, secondary metabolites, phytochemical, physiology, enzyme, toxicity

Citation

Senthil-Nathan S (2020) A Review of Resistance Mechanisms of Synthetic Insecticides and Botanicals, Phytochemicals, and Essential Oils as Alternative Larvicidal Agents Against Mosquitoes. Front. Physiol. 10:1591. doi: 10.3389/fphys.2019.01591

Received

20 May 2019

Accepted

19 December 2019

Published

25 February 2020

Volume

10 - 2019

Edited by

Sylvia Anton, Institut National de la Recherche Agronomique (INRA), France

Reviewed by

Jose Eduardo Serrão, Universidade Federal de Viçosa, Brazil; Samar Ramzi, Agricultural Research, Education and Extension Organization (AREEO), Iran

Updates

Copyright

*Correspondence: Sengottayan Senthil-Nathan, ;

This article was submitted to Invertebrate Physiology, a section of the journal Frontiers in Physiology

Disclaimer

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.

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