Deviation in the Metabolite Activity and Decreases in Escherichia coli Load in Anopheles Mosquitoes After Feeding with Blood Meal Treated with Nanocurcumin
Special Issue:
Emerging and Re-emerging Animal Health Challenges in Low and Middle-Income Countries
Deviation in the Metabolite Activity and Decreases in Escherichia coli Load in Anopheles Mosquitoes After Feeding with Blood Meal Treated with Nanocurcumin
Sura Saad Hamada Alkhuzaie
Department of Veterinary Microbiology, College of Veterinary Medicine, University of Al-Qadisiyah, Al-Diwaniyah, Iraq.
Abstract | The current study was performed to identify changes in metabolic activities and to measure the load of pathogens of E. coli as an example, in Anopheles mosquitoes after feeding with nanocurcumin-treated blood meal (NBM). The study included the use of 216 female mosquitoes divided randomly into six replicates for each group. The groups were a 6hr-ealier provision of NBM before E. coli exposure, the 6E group, in which NBM was provided to mosquitoes 6hrs before bacterial exposure. There was a group in which both E. coli exposure (ECE) and NBM were provided at the same time, the 0T group. In addition, there was a 6hr-laterNBM provision after ECE, the 6L group. Moreover, there was a 24hr-laterNBM provision after ECE in the 24L group. Finally, there were control groups, in which one group was supplied with sterile water only, the SW group, and a group that received no-NBM but ECE only, the nNBM group. For all treatments, NBM or ECE was only continued for 30 min. After the end of the experiment (24hrs after the supply of the NBM), the midgut of each mosquito was dissected. A test of the E. coli colony-forming units (CFUs) was performed for all groups. The metabolites were detected using mass spectrometry (MS). The results revealed significant (p<0.05) increases in the E. coli CFUs of the NNBM group when compared with those from the SW group. These levels decreased significantly (p<0.05) in all groups, especially in the 0T group. In the case of the metabolic activity, significant (p<0.05) increases were seen in the abundance of pantothenic acid, proline, and trehalose in the groups treated with NBM. The current study provides important findings that nanocurcumin shows protective and treatment activities against E. coli load and that comes with increases in the abundance of certain important metabolites in the midgut of mosquitoes.
Keywords | Anopheles, Mosquito-borne infections, Herbal insecticides
Received | August 28, 2024; Accepted | November 18, 2024; Published | December 12, 2024
*Correspondence | Sura Saad Hamada Alkhuzaie, Department of Veterinary Microbiology, College of Veterinary Medicine, University of Al-Qadisiyah, Al-Diwaniyah, Iraq; Email: [email protected]
Citation | Alkhuzaie SSH (2024). Deviation in the metabolite activity and decreases in Escherichia coli load in Anopheles mosquitoes after feeding with blood meal treated with nanocurcumin. J. Anim. Health Prod. 12(s1): 338-343.
DOI | https://dx.doi.org/10.17582/journal.jahp/2024/12.s1.338.343
ISSN (Online) | 2308-2801
Copyright: 2024 by the authors. Licensee ResearchersLinks Ltd, England, UK.
This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Introduction
The presence of insect species presents several challenges to human and animal well-being, including potential threats to human health, food security, the preservation of threatened species, economic ramifications, and the sustainability of environments (Zhang et al., 2022). These species are sometimes referred to as exotic or imported organisms. Whether intentionally, accidentally, or via commerce, the human species is to blame for their emergence (Venette and Hutchison, 2021). In addition to the evident threat they pose to biodiversity, the introduction of these insects also presents a substantial threat to the biosecurity of a country (Siddiqui et al., 2021). The fast growth of global commerce and human networking has facilitated the unprecedented transportation of species to previously untouched places around the planet. The recognition of the detrimental impacts of introduced species on indigenous biodiversity and the subsequent revenue losses in several countries has seen an upward trajectory in the last twenty years (Rao et al., 2018). Recent studies on the evolutionary genetics of invading species have shown that the capacity to adapt to natural selection could have more significance in facilitating the effective colonization of some imported species compared to general physiological flexibility or tolerance (Pimental et al., 2005; Marbuah et al., 2014). Consequently, the accidental consequence of this phenomenon is the enhancement of the invasive species’ capacity for evolution, facilitating its rapid proliferation and geographic expansion within the introduced region (Lavergne and Molofsky, 2007; Hafez et al., 2022).
The persistence of illnesses transmitted by mosquitoes continues to pose a significant challenge to global public health since the development of effective vaccinations and treatments for many diseases remains limited (Reid and Mckenzie, 2016; Jawad and Alfatlawi, 2023). However, it is important to note that these illnesses may be prevented by measures such as the avoidance of mosquito bites and the elimination of possible vectors using pesticides (Richards et al., 2017; Dusfour et al., 2019). These strategies are considered essential components of integrated mosquito management (IMM) and have a significant role in reducing the incidence of these diseases. Nevertheless, the occurrence of control failures may be attributed to variables such as insecticide resistance (IR), inadequate pesticide application processes, and several other factors. It is worth noting that the underreporting of these failures might be partially attributed to resource constraints (Corbel et al., 2016; Jasim et al., 2023). Regular and efficient monitoring of mosquitoes for IR is crucial in order to gather information that may guide choices on mosquito management (Corbel et al., 2019; Jawad and Alfatlawi, 2023).
Mosquitoes encounter insecticides from different sources, including government-operated vector control programs, private pest control services for households, and commercial establishments, as well as approaches in agricultural settings (Depres et al., 2007; Dunbar et al., 2018).
Environmental researchers and agriculturalists possess knowledge of the enduring consequences of pesticides and the ramifications of the release of toxic chemicals into the environment. The rising prevalence of cancers and other chronic illnesses during the last half-century or so may be linked not only to increasing numbers of people but also to the use of pesticidal substances, which may enhance the effects of carcinogens (Jordahl et al., 1997; Li et al., 2008; Yadav et al., 2015). Wetland polluted with pesticidal waste poses a significant risk to both the aquatic ecology and drinking water supplies. Water pollution is a phenomenon characterized by the detrimental impact on water bodies resulting from the introduction of substantial amounts of foreign substances into waterways. Several remediation techniques, including leaching and landfilling, have been used to mitigate the adverse effects caused by the deposition of hazardous chemical contaminants in soil. Nevertheless, the implementation of soil remediation techniques including the elimination of harmful substances and the treatment of debris is both labour-intensive and financially burdensome (Gianfreda and Rao, 2004; Jie and Conrad, 2009; Jacobsen and Hjeluso, 2014; Cycon et al., 2019; Jayaraj et al., 2019).
The present scholarly investigations in the field of mosquito control are now fouced on comprehending the resistance of mosquitoes to synthetic pesticides and inventing innovative approaches to address these resistance concerns. The scientific community is increasingly focused on natural chemicals that exhibit superior efficacy and lower toxicity compared to their synthetic counterparts. The application of bioinsecticides, which consist of botanical or plant-derived substances, has emerged as a viable option owing to their limited adverse impacts on human well-being and the surrounding environment (Adeleke et al., 2008; Ayilara et al., 2014; Laxmishree and Nandita, 2017).
The current study was performed to identify changes in the metabolic activities and to measure the load of pathogens, E. coli as an example, in Anopheles mosquitoes after feeding with nanocurcumin-treated blood meal (NBM). Some important applications of nanocurcumin are wound healing, anti-inflammatory effects, drug delivery, antioxidant effects, etc. (Laxmishree and Nandita, 2017). Synthesis methods of nano-curcumin can be categorized as traditional methods and new and upcoming methods. In the traditional methods of nano-curcumin, the methods are: the ultrasonication method, sonicated nano-emulsion, the co-precipitation method, solvent-evaporation, solvent diffusion, the nanoprecipitation method, the simple solvent diffusion method, the micro-emulsification solvent evaporation method, the emulsion-diffusion method, the rotating pin micro-emulsification method, and the supercritical fluid technologies. In 2009, the first curcumin nanoparticles were produced by coating the curcumin complex with polymer-encasing nanoparticles. Very few methods for nano-curcumin have been reported in the literature.
Curcumin can also be dissolved in mono-, di-, and triglycerides, and then simply be atomized to yield nanoemulsions of curcumin. This method yields the nanoemulsion, which is a thermodynamically controlled stable carrier system with high bioactivity. In the nanoemulsion process, tricurin is not dissolved but exposed to an internal surface, which is very large and responsible for the water solubility of curcumin. This method is in principle quite simple and only a mixer is required. To further scale up the production of tricurin, an electrostatic atomizer is required, which is commercially available and has a capacity of several liters per hour.
Materials and Methods
Experiment
The study included the use of 216 female mosquitoes (a few numbers were reared until reached a number higher than 216) divided randomly into 6 replicates for each group. Nanocurcumin was used from an industry product bought locally. The groups were a 6hr-ealier provision of NBM before E. coli exposure, 6E group, in which NBM was provided to mosquitoes 6hrs before bacterial exposure. There was a group, in which both ECE and NBM were provided at the same time, 0T group. In addition, there was a 6hr-later-NBM provision after ECE, 6L group. Moreover, there was a 24hr-later-NBM provision after ECE, 24L group. Finally, there were control groups, in which one group was supplied with sterile water only, SW group, and a group that received no-NBM but ECE only, NNBM group. For all treatments, NBM (8µg/ml) (Negahdari et al., 2020) or ECE (1%) (Souvannaseng et al., 2018) was only continued for 30 min. After the end of the experiment (24 h after the supply of the NBM), the midgut for each mosquito was dissected.
E. coli colony forming unit and mass spectrometry
A test of the E. coli CFUs was performed for all groups according to Othman et al. (2023). The metabolites were detected using MS based on methods by Souvannaseng et al. (2018).
Statistical analysis
The study data were analyzed and graphed using GraphPad Prism (v9). The Mean±SEM was used to present data. The level of p less than 5% was followed. A one-way ANOVA test was done.
Results and Discussion
The results revealed significant (p<0.05) increases in the E. coli CFUs of the NNBM group when compared with these from the SW group. These levels decreased significantly (p<0.05) in all groups, especially in the 0T group (Figure 1).
Table 1 represents the CFU for each group with their rates.
Table 1: CFU of E. coli in each group.
Group |
CFU (x1000) |
Percentage Reduction |
SW |
10 |
67% |
NNBM |
30 |
0% |
6E |
25 |
17% |
0T |
20 |
33% |
6L |
22 |
27% |
24L |
30 |
0% |
In the case of the metabolic activity, significant (p<0.05) numbers of metabolites increased in their abundance in the groups treated with NBM, such as pantothenic acid, proline, and trehalose, while a low number of compounds faced decreases in their abundance (data not shown) (Figure 2).
In the case of the metabolic activity, significant (p<0.05) increases were seen in the abundance of pantothenic acid, proline, and trehalose in the groups treated with NBM (Figure 3).
The present study revealed increases in the presence percentages of E. coli in the exposure group; however, these increases showed declines when nanocurcumin was introduced. Curcumin is a classic medicinal substance that is frequently employed in several biological applications. Nanotechnology is being explored as a potential solution to enhance the effective utilization of curcumin. The inherent physicochemical properties of curcumin, including chemical instability, limited bioavailability, and poor water solubility, pose challenges to its pharmaceutical application. To address these limitations and enhance the therapeutic efficacy of curcumin, the utilization of nanotechnology is being investigated as a promising avenue (Chowanski et al., 2016; Balachandran et al., 2021).
A multitude of studies have shown the efficacy of curcumin in combating a diverse range of bacteria. The antimicrobial effect described in this study utilizes a multi-mechanistic approach, which involves the interaction between the nanoparticles and the membrane of the bacterium. This reaction leads to the formation of localized pores in the membrane, allowing the passage of nanoparticles into the cells of the bacteria. Once inside, these nanoparticles engage with intracellular protein molecules, thereby jeopardizing bacterial tasks (Mohanty and Sahoo., 2020). Another potential mechanism involves the attachment of nanoparticles to the microorganism membrane, followed by gradually implemented penetration into their cytoplasm and subsequent disruption of bacterial activities (Passos et al., 2013).
In contrast, currently employed antibiotics typically act through a limited number of mechanisms, rendering them susceptible to microbial resistance. These outcomes are consistent with previous studies by Gopal et al. (2016) and No et al. (2017), which reported that nanosized component elements exhibit greater cellular mobilization compared to their larger colleagues. The antibacterial effect was higher for the nanotechnology particle concentration of the current study than those by Othman et al. (2023) at (15.65-31.25 µg/mL) and by No et al. (2017) at (125-250 µg/mL).
In the case of the changes in the levels of metabolites, the current work revealed alterations accompanied the use of nanocurcumin. These changes may provide information related to increase resistance of mosquito digestive system to the presence of E. coli. This can be assured via increases in the levels of pantothenic acid, proline, and trehalose, in which these last two compounds represent fuels for a healthy mosquito instead of using glucose as a substrate and fuel the TCA cycle that could increase in an infected mosquito (Arrese and Soulages, 2010; Teulier et al., 2016; Giulivi et al., 2018; Tang et al., 2018; Batista et al., 2021; Leyria et al., 2021; Stec et al., 2021).
Conclusion
The current study provides important findings that nanocurcumin shows protective and treatment activities against E. coli load and that comes with increases in the abundance of certain important metabolites in the midgut of the mosquitoes.
Acknowledgments
Very special gratitude to Prof. Dr. Alsaadi Jabar Abbas, Faculty of Veterinary Medicine, University of Al-Qadisiyah.
Novelty Statement
The nanocurcumin shows protective and treatment activities against E. coli load.
Conflict of interest
The authors have declared no conflict of interest.
References
Adeleke BS, Ayilara MS, Akinola SA, Fayose CA, Adeyemi UT, Gbadegesin LA (2008). Frontiers, biopesticides as a promising alternative to synthetic pesticides: A case for microbial pesticides, phytopesticides, and nanobiopesticides. Front. Microbiol., 5(1): 14. https://doi.org/10.3389/fmicb.2023.1040901
Arrese EL, Soulages JL (2010). Insect fat body: energy, metabolism, and regulation. Ann. Rev. Entomol., 55(1): 207–225. https://doi.org/10.1146/annurev-ento-112408-085356
Ayilara MS, Adeleke BS, Akinola SA, Fayose CA, Adeyemi UT, Gbadegesin LA (2014). Biopesticides as a promising alternative to synthetic pesticides: A case for microbial pesticides, phytopesticides, and nanobiopesticides. Front. Microbiol., 5(1): 14. https://doi.org/10.3389/fmicb.2023.1040901
Balachandran C, Anbalagan S, Kandeepan C, Arun-Nagendran N, Jayakumar M, Fathi Abd-Allah E, Alqarawi AA, Hashim A, Baskar K (2021). Molecular docking studies of natural alkaloids as acetylcholinesterase (AChE1) inhibitors in Aedes aegypti. J. Asia Pac. Entomol., 24(3): 645–652. https://doi.org/10.1016/j.aspen.2021.05.011
Batista de Andrade Neto J, Pessoa de Farias Cabral V, Brito Nogueira LF, Rocha da Silva C, Gurgel do Amaral Valente Sá L, Ramos da Silva A (2021). Anti-MRSA activity of curcumin in planktonic cells and biofilms and determination of possible action mechanisms. Microb. Pathog., 155(1): 104892. https://doi.org/10.1016/j.micpath.2021.104892
Chowański S, Adamski Z, Marciniak P, Rosiński G, Büyükgüzel E, Büyükgüzel K, Scrano L, Lelario F (2016). A review of bioinsecticidal activity of solanaceae alkaloids. Toxins (Basel), 8(3): 60. https://doi.org/10.3390/toxins8030060
Corbel V, Achee NL, Chandre F, Coulibaly MB, Dusfour I, Fonseca DM, Grieco J, Juntarajumnong W, Lenhart A, Martins A, Moyes C, Ng LC, Pinto J, Raghavendra K, Vatantoost H, Vontas J, Weetman D, Fouque F, Velayudhan R, David J (2016). Tracking insecticide resistance in mosquito vectors of arboviruses: The worldwide insecticide resistance network (WIN). PLoS Negl. Trop. Dis., 10(12): e0005054. https://doi.org/10.1371/journal.pntd.0005054
Corbel V, Durot C, Achee NL, Chandre F, Coulibaly MB, David JP, Dusfour I, Griego J, Kasai S, Martins A, Ng LC, Roiz D (2019). Second WIN International Conference on “Integrated approaches and innovative tools for combating insecticide resistance in vectors of arboviruses. Parasit. Vectors, 12(1): 331. https://doi.org/10.1186/s13071-019-3591-8
Cycoń M, Wójcik M, Borymski S, Piotrowska-Seget Z (2019). Short-term effects of the herbicide napropamide on the activity and structure of the soil microbial community assessed by the multi-approach analysis. Appl. Soil Ecol., 66(1): 8–18. https://doi.org/10.1016/j.apsoil.2013.01.014
Després L, David JP, Gallet C (2007). The evolutionary ecology of insect resistance to plant chemicals. Trends Ecol. Evol., 22(6): 298–307. https://doi.org/10.1016/j.tree.2007.02.010
Dunbar MW, Bachmann A, Varenhorst AJ (2018). Reduced insecticide susceptibility in Aedes vexans (Diptera: Culicidae) where agricultural pest management overlaps with mosquito abatement. J. Med. Entomol., 55(3): 747–751. https://doi.org/10.1093/jme/tjx245
Dusfour I, Vontas J, David JP, Weetman D, Fonseca DM, Corbel V, Corbel V, Kamarajo R, Coulibaly MB, Martins A, Kasai S, Chandre F (2019). Management of insecticide resistance in the major Aedes vectors of arboviruses: Advances and challenges. PLoS Negl. Trop. Dis., 13(10): e0007615. https://doi.org/10.1371/journal.pntd.0007615
Gianfreda L, Rao MA (2004). Potential of extra cellular enzymes in remediation of polluted soils: A review. Enzyme Microbial. Technol., 35(4): 339–354. https://doi.org/10.1016/j.enzmictec.2004.05.006
Giulivi C, Ross-Inta C, Horton AA, Luckhart S (2018). Metabolic Pathways in Anopheles stephensi mitochondria. Biochem. J., 415(2): 309–316. https://doi.org/10.1042/BJ20080973
Gopal J, Muthu M, Chun S (2016). Bactericidal property of macro-, micro- and nanocurcumin: An assessment. Arab J. Sci. Eng., 41(6): 2087–2093. https://doi.org/10.1007/s13369-015-1834-3
Hafeez M, Ullah F, Khan MM, Li X, Zhang Z, Shah S, Imran M, Assiri M, Grandon GM, Desneux N, Rehman M, Fahad S, Lu Y (2022). Metabolic-based insecticide resistance mechanism and ecofriendly approaches for controlling of beet armyworm Spodoptera exigua: A review. Environ. Sci. Pollut. Res. Int., 29(2): 1746–1762. https://doi.org/10.1007/s11356-021-16974-w
Jacobsen CS, Hjelmsø MH (2014). Agricultural soils, pesticides and microbial diversity. Curr. Opin. Biotechnol., 27(1): 15–20. https://doi.org/10.1016/j.copbio.2013.09.003
Jasim GA, Alfatlawi MA, Chaid ZH (2023). Microscopic and molecular detection of Babesia bovis and Babesia bigemina in female camel from Al-Diwaniyah province, Iraq. Iraqi J. Vet. Sci., 37(1): 61–64. https://doi.org/10.33899/ijvs.2022.133428.2226
Jawad AQ, Alfatlawi MA (2023). Detection of the cytochrome B (cytb) insecticide resistance gene in Theileria annulata isolated from cattle in Hilla city, Babylon governorate, Iraq. Iraqi J. Vet. Sci., 37(Supplement I-IV):153–158. https://doi.org/10.33899/ijvs.2023.137902.2749
Jawad AQ, Alfatlawi MAA (2023). Molecular study and DNA sequence analysis of Theileria annulata in cattle in Al-Hilla, Iraq. Iraqi J. Vet. Sci., 37(2): 425–429. https://doi.org/10.33899/ijvs.2022.135154.2450
Jayaraj R, Megha P, Sreedev P (2019). Organochlorine pesticides, their toxic effects on living organisms and their fate in the environment. Interdiscip. Toxicol., 9(3–4): 90–100. https://doi.org/10.1515/intox-2016-0012
Jia Z, Conrad R (2009). Bacteria rather than Archaea dominate microbial ammonia oxidation in an agricultural soil. Environ. Microbiol., 11(7): 1658–1671. https://doi.org/10.1111/j.1462-2920.2009.01891.x
Jordahl JL, Foster L, Schnoor JL, Alvarez PJJ (1997). Effect of hybrid poplar trees on microbial populations important to hazardous waste bioremediation. Environ. Toxicol. Chem., 16(6): 1318–1321. https://doi.org/10.1002/etc.5620160630
Lavergne S, Molofsky J (2007). Increased genetic variation and evolutionary potential drive the success of an invasive grass. Proc. Natl. Acad. Sci., 104(10): 3883–3888. https://doi.org/10.1073/pnas.0607324104
Laxmishree C, Nandita S (2017). Botanical pesticides a major alternative to chemical pesticides: A review. Int. J. Life Sci., 5(4): 722–729.
Leyria J, El-Mawed H, Orchard I, Lange AB (2021). Regulation of a trehalose-specific facilitated transporter (TRET) by insulin and adipokinetic hormone in Rhodnius prolixus, a vector of chagas disease. Front. Physiol., 12(1): 624165. https://doi.org/10.3389/fphys.2021.624165
Li XH, Wang W, Wang J, Cao XL, Wang XF, Liu JC, Xu XB, Jiang X (2008). Contamination of soils with organochlorine pesticides in urban parks in Beijing, China. Chemosphere, 70(9): 1660–1668. https://doi.org/10.1016/j.chemosphere.2007.07.078
Marbuah G, Gren IM, McKie B (2014). Economics of harmful invasive species: A review. Diversity, 6(3): 500–523. https://doi.org/10.3390/d6030500
Mohanty C, Sahoo SK (2020). The in vitro stability and in vivo pharmacokinetics of curcumin prepared as an aqueous nanoparticulate formulation. Biomaterials, 31(25): 6597–6611. https://doi.org/10.1016/j.biomaterials.2010.04.062
Negahdari R, Ghavimi MA, Barzegar A, Memar MY, Balazadeh L, Bohlouli S, Sharifi S, Dizaj SM (2020). Antibacterial effect of nanocurcumin inside the implant fixture: An in vitro study. Clin. Exp. Dent. Res., 7(2): 163–169. https://doi.org/10.1002/cre2.348
No DS, Algburi A, Huynh P, Moret A, Ringard M, Comito N, Drider D, Takhistov P, Chikindas ML (2017). Antimicrobial efficacy of curcumin nanoparticles against Listeria monocytogenes is mediated by surface charge. J. Food Saf., 37(4): e12353. https://doi.org/10.1111/jfs.12353
Othman AS, Shamekh IM, Abdalla M, Eltayb WA, Ahmed NA (2023). Molecular modeling study of micro and nanocurcumin with in vitro and in vivo antibacterial validation. Sci. Rep., 13(1): 12224. https://doi.org/10.1038/s41598-023-38652-2
Passos SP, Gressler May L, Faria R, Özcan M, Bottino MA (2013). Implant-abutment gap versus microbial colonization: Clinical significance based on a literature review. J. Biomed. Mater. Res. B. Appl. Biomater., 101(7): 1321–1328. https://doi.org/10.1002/jbm.b.32945
Pimentel D, Zuniga R, Morrison D (2005). Update on the environmental and economic costs associated with alien-invasive species in the United States. Ecol. Econ., 52(3): 273–288. https://doi.org/10.1016/j.ecolecon.2004.10.002
Rao NC, Roshan DR, Rao GK, Ramanandam GA (2018). Review on rugose spiralling whitefly, Aleurodicus rugioperculatus martin (Hemiptera: Aleyrodidae) in India. J. Pharmacogn. Phytochem., 7(5): 948–953.
Reid MC, McKenzie FE (2016). The contribution of agricultural insecticide uses to increasing insecticide resistance in African malaria vectors. Malar J., 15(1): 107. https://doi.org/10.1186/s12936-016-1162-4
Richards SL, Balanay JAG, Byrd BD, Reiskind MH, Styers DM (2017). Regional survey of mosquito control knowledge and usage in North Carolina. J. Am. Mosq. Contr. Assoc., 33(4): 331–339. https://doi.org/10.2987/17-6669.1
Siddiqui JA, Bamisile BS, Khan MM, Islam W, Hafeez M, Bodlah I, Xu Y (2021). Impact of invasive ant species on native fauna across similar habitats under global environmental changes. Environ. Sci. Pollut. Res. Int., 28(39): 54362–54382. https://doi.org/10.1007/s11356-021-15961-5
Souvannaseng L, Hun LV, Baker H, Klyver JM, Wang B, Pakpour N, Napoli N, Gulivi C, Luckhart S (2018). Inhibition of JNK signaling in the Asian malaria vector Anopheles stephensi extends mosquito longevity and improves resistance to Plasmodium falciparum infection. PLoS Pathog., 14(11): e1007418. https://doi.org/10.1371/journal.ppat.1007418
Stec N, Saleem A, Darveau CA (2021). Proline as a sparker metabolite of oxidative metabolism during the flight of the bumblebee, Bombus impatiens. Metabolites, 11(8): 511. https://doi.org/10.3390/metabo11080511
Tang B, Wang S, Wang SG, Wang HJ, Zhang JY, Cui SY (2018). Invertebrate trehalose-6-phosphate synthase gene: Genetic architecture, biochemistry, physiological function, and potential applications. Front. Physiol., 9(1): 30. https://doi.org/10.3389/fphys.2018.00030
Teulier L, Weber JM, Crevier J, Darveau CA (2016). Proline as a fuel for insect flight: Enhancing carbohydrate oxidation in hymenopterans. Proc. Biol. Sci., 283(1834): 20160333. https://doi.org/10.1098/rspb.2016.0333
Venette RC, Hutchison WD (2021). Invasive insect species: Global challenges, strategies and opportunities. Front. Insect Sci., 2021(1): 650520. https://doi.org/10.3389/finsc.2021.650520
Yadav IC, Devi NL, Syed JH, Cheng Z, Li J, Zhang G, Johnes KC (2015). Current status of persistent organic pesticides residues in air, water, and soil, and their possible effect on neighboring countries: A comprehensive review of India. Sci. Total Environ., 511(1): 123–137. https://doi.org/10.1016/j.scitotenv.2014.12.041
Zhang S, Zhou Y, Yu R, Xu X, Xu M, Li G, Wang W, Yang Y (2022). China’s biodiversity conservation in the process of implementing the sustainable development goals (SDGs). J. Cleaner Prod., 338(1): 130595. https://doi.org/10.1016/j.jclepro.2022.130595
To share on other social networks, click on any share button. What are these?