Accepted Manuscript Bluetongue outbreaks: Looking for effective control strategies against Culicoides vectors
Giovanni Benelli, Luca Buttazzoni, Angelo Canale, Armando D'Andrea, Paola Del Serrone, Gavino Delrio, Cipriano Foxi, Susanna Mariani, Giovanni Savini, Chithravel Vadivalagan, Kadarkarai Murugan, Chiara Toniolo, Marcello Nicoletti, Mauro Serafini PII: DOI: Reference:
S0034-5288(17)30314-4 doi: 10.1016/j.rvsc.2017.05.023 YRVSC 3339
To appear in:
Research in Veterinary Science
Received date: Revised date: Accepted date:
16 March 2017 18 May 2017 19 May 2017
Please cite this article as: Giovanni Benelli, Luca Buttazzoni, Angelo Canale, Armando D'Andrea, Paola Del Serrone, Gavino Delrio, Cipriano Foxi, Susanna Mariani, Giovanni Savini, Chithravel Vadivalagan, Kadarkarai Murugan, Chiara Toniolo, Marcello Nicoletti, Mauro Serafini , Bluetongue outbreaks: Looking for effective control strategies against Culicoides vectors, Research in Veterinary Science (2017), doi: 10.1016/ j.rvsc.2017.05.023
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Review
Bluetongue outbreaks: looking for effective control strategies against
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Culicoides vectors
Giovanni Benelli 1*, Luca Buttazzoni 2, Angelo Canale 1, Armando D’Andrea 3, Paola Del Serrone 2, Gavino Delrio 4, Cipriano Foxi 4, Susanna Mariani 3, Giovanni Savini 5, Chithravel Vadivalagan 6, Kadarkarai Murugan 6, Chiara Toniolo 7, Marcello Nicoletti 7,
Department of Agriculture, Food and Environment, University of Pisa, Via del
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Borghetto 80, 56124 Pisa, Italy 2
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Mauro Serafini 7
Council for Agricultural Research and Economics (CREA), Animal Production
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C. R. ENEA Casaccia, SSPT-TECS-BIORISC, Via Anguillarese 301, 00123, S. M.
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Galeria, Roma, Italy
Dipartimento di Agraria, Sezione di Patologia Vegetale ed Entomologia, Università
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Research Centre, Via Salaria 31, 00016 Monterotondo Scalo, Roma, Italy
degli Studi di Sassari, Via Enrico de Nicola, 07100 Sassari, Italy. 5
Istituto Zooprofilattico dell’Abruzzo e del Molise “G. Caporale”, Via Campo Boario, 64100 Teramo, Italy.
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Division of Entomology, School of Life Sciences, Bharathiar University, Coimbatore641046, Tamil Nadu, India
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Department of Environmental Biology, Sapienza University, Sapienza University of Rome, Piazzale Aldo Moro 5, 00185 Rome, Italy
* Corresponding author. Tel.: +39-0502216141. Fax: +39-0502216087. E-mail address:
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[email protected]
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Abstract
Several arthropod-borne diseases are now rising with increasing impact and risks for public health, due to environmental higher changes and resistance to pesticides
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currently marketed. In addition to community surveillance programs and a careful management of herds, a next-generation of effective products is urgently needed to control the spread of these diseases. Natural product research can afford alternative solutions. Recently, a re-emerging of bluetongue disease is ongoing in Italy. Bluetongue is a viral disease that affects ruminants and is spread through the bite of bloodsucking
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insects, especially Culicoides species. In this review, we focused on the importance of
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vector control programs for prevention or bluetongue outbreaks, outlining the lack of effective tools in the fight against Culicoides vectors. Then, we analyzed a field case
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study in Sardinia (Italy) concerning the utilization of the neem cake (Azadirachta indica), to control young instar populations of Culicoides biting midges, the vectors of
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bluetongue virus. Neem cake is a cheap and eco-friendly by-product obtained from the extraction of neem oil. Overall, we propose that the employ of neem extraction by-
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products as aqueous formulation, in muddy sites close to livestock grazing areas, may
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represent an effective tool in the fight against the spread of bluetongue virus in the Mediterranean areas.
Keywords: arthropod-borne diseases; biosafety; botanical; biting midge; Ceratopogonidae; neem cake
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1. Introduction
Currently, the control of arthropod-borne diseases represent one of the major challenges of medical and veterinary importance (WHO 2000; Benelli 2015a). Several
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factors are nowadays flowing into global and national emergencies, in particular for farm animals. After a long period dominated by intensive livestock farming, supported by massive use of insecticides and antibiotics production levels are nowadays in danger (Mehlhorn 2012). The indications are that several new situations, like international trade, globalization, and massive migrations, are important biotic factors that pose
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vector-borne animal diseases as a continuous threat to livestock economies worldwide
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(Ebers et al. 2015). Notably, pesticides currently marked for vector control have to face the rapid development of resistance, besides leading to important problems for human
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and animal health, as well as non-target effects on the environment (Hemingway and Ranson 2000; Isman et al. 2006; Naqqash et al. 2016; Pavela and Benelli 2016a,b).
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The rapid diffusion of arthropod-borne disease is the result of the cooccurrence of at least three factors: environmental changes, boosted vector efficiency,
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and selection of more aggressive pathogens and parasites, thanks to their rapid adaption
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to novel hosts (Bethan 2005). A reliable way to tackle these issues is to face the problem with an integrated multidisciplinary approach (Nicoletti et al. 2012b). As recently highlighted by the Centers for Disease Control and Prevention, to successfully fight arthropod-borne diseases, a One Health approach is important (Day 2011; DantasTorres et al. 2012). One Health pointed out that the human health is strongly connected to the health of animals and the environment care. One Health intends encourage the
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cooperation among multiple disciplines, protecting human health and the environment (Franco et al. 2014; Webster et al. 2016). Bluetongue is a viral disease that affects ruminants and is spread through the bite of bloodsucking insects (Mordue e al. 2007). This mechanism is common to many
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insect-borne diseases affecting humans, such as malaria, West Nile virus and the recent Zika virus, or animals, as the Schmallenberg virus, Usutu virus and viral hemorrhagic fever. In these cases, micro-organisms and other infectious agents develop in the cells of vertebrate organisms (Benelli and Mehlhorn 2016; Benelli et al. 2016a,b). Biting midges, belonging to the genus Culicoides (Diptera: Ceratopogonidae),
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can feed on viremic animals, transmitting the infection caused by the bluetongue virus
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to livestock, as well as wild ruminant populations (Wilson and Mellor 2009; Carpenter et al. 2013). These insects are bad fliers, but being lightweight, they can be carried by
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wind over long distances (Ducheye 2007; see also Bhasin and Mordue 2000 and Rasmussen et al. 2012). The spread of the disease can also occur with the transport of
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infected animals. However, the tentative of blocking the movements of receptive animals is not always able to prevent the spread of bluetongue. Furthermore, it affects
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the sale of the animals, creating serious socio-economic damages to farmers (Wilson
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and Mellor 2009).
In Italy, the bluetongue disease appeared in 2000, probably favored by wind
translocation of infected Culicoides vectors from North Africa (Wilson and Mellor 2009). Although bluetongue initially affected Sicily and Calabria (Southern Italy), then spread out in Sardinia, the second main island of Italy, where became virtually endemic and caused the death of hundreds of thousands of sheep of high economic value (Foxi and Delrio 2010).
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Despite the preventive actions taken, mainly consisting in restriction of movement of animals and massive vaccination program, the bluetongue infection continued to spread in the Italian peninsula, affecting the entire South and Central Italy, and rapidly spreading to the North of Italy, although Sardinia remained the most
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damaged (Nicoletti et al. 2014). Since 2006, the bluetongue, as bluetongue serotype 8, has also been reported in the Netherlands, Belgium, Germany, France, Bulgaria and United Kingdom, where it was particularly virulent on cattle (Elbers et al. 2008; Gloster et al. 2008), involving also the Northern regions of Europe, like Scotland (Hendry and Godwin 1988; Kettle 1951, 1995) with several negative effects (Blackwell et al. 2004;
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Carpenter et al. 2013).
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As a general trend, even cattle and goats become infected, but they are often asymptomatic. In sheep, however, the disease manifests itself in different clinical forms
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of hyper-acute, with a lethality of up to 30%, and sub-clinical, in which case the sick animals recover in a few days with complete remission of symptoms. The presence of
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viral particles in the blood of sheep, which reaches a peak 7-8 days after infection, usually does not exceed thirty days, whereas in cattle can persist for about 60 days
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(Schwartz-Cornil et al. 2008). In this period, the infected animal acts as reservoir of the
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virus, and is used by the insect vector as intermediate step to spread the disease (Schwartz-Cornil et al. 2008).
2. Current tools in the fight against bluetongue
In many countries, wherein the bluetongue disease and its insect vectors are present or expected, an effective monitoring system (Mands et al. 2004; Gerry et al.
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2009; Nielsen et al. 2010; Thompson et al. 2014; Murchie et al. 2016) can allow to identify new strains of the virus and carefully following the spread of serotypes already in the territory, as well as invasion of new regions. This is an aspect of fundamental importance, since the infection by a serotype does not protect against further infection
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by different viral serotypes (Perrin et al. 2007). The entomological surveillance national plan aims to identify the geographical distribution and seasonal dynamics of insect vectors through the placement of light traps on farms (Mordue et al. 2007). The insect catches are analyzed for quantization of total Culicoides and to determine the presence/absence of C. imicola, the main vector of
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bluetongue in sheep, both in the protection and surveillance zones and in the high-risk
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areas (Goffredo and Meiswinkel 2004). This vector is widespread in the warmer coastal areas of central and southern Italy. However, in recent years the presence of other
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vector species, such as C. obsoletus, C. scoticus, C. dewulfi, C. newsteadi, C. pulicaris and C. punctatus, has been reported, with a wider distribution also affecting northern
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areas (Goffredo et al. 2015; Foxi et al. 2016). In Italy, the National Veterinary Epidemiological Bulletin reported outbreaks of bluetongue in 2015 and the first quarter
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of 2016, as observed in several Italian regions (IZSM&A 2016a,b).
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In the future, the bluetongue outbreaks could spread more rapidly if compared to the past, due to climate change, with periods characterized by the persistence of high temperatures that accompany rains, and consequently high humidity. These conditions also favor early spring and late fall larval development, consequently leading to the increase in Culicoides vector populations and the risk of disease transmission. After a period of relative calm, in 2016-2017 a new upsurge of the bluetongue emerged in Sardinia. To counter the resurgence of the disease, more than a million vaccines were
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produced. However, to avoid a continuous recourse to vaccination in an illness that recurs periodically, this intervention must be accompanied by prevention and by combating vectors in periods of stasis (Foxi et al. 2016). The control of Culicoides is currently limited to the treatments with synthetic
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insecticides against adults on the stable walls or using treated nets (Narladkar et al. 2006; Mordue et al. 2007; Carpenter et al. 2008; Bauer et al. 2009; Del Rìo et al. 2014a,b, Baker et al. 2015; De Keyser et al. 2017), in potential synergy with animal housing (Baylis et al. 2010) and mechanical disturbance of Culicoides emergence from cowpats (Lühken et al. 2014, 2015). Notably, insecticidal treatments with synthetic
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pesticides are currently facing the possible development of resistance in targeted pests
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(Naqqash et al. 2016), which can strongly limit the effectiveness of control programs (De Keyser et al. 2017).
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A further option can be the treatment directly on animals with repellent products, with special reference to N, N-diethyl-meta-toluamide, (DEET), para-
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menthane-3, 8-diol (PMD) and citronella (Cymbopogon citratus L.) oil (Braverman et al. 1997, 2000, 2004; Calvete et a. 2010; Schmahl et al. 2008; Martínez-de la Puente et
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al. 2009; Page et al. 2009, 2014; Venter et al. 2011; González et al. 2014; Murchie et al.
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2016). However, the continuous protection of livestock with repellents is a difficult challenge, which lead to uncertain results (Narladkar et al. 2006; Carpenter et al. 2008). A good example has been reported by Page et al. (2009), in field assays testing 15% (DEET), 0.6% citronella oil, and 0.3% alpha-cyano-cypermethrin against Culicoides species. The three products were applied to polyester meshes fitted to down-draught suction 220V UV light traps operating overnight. Notably, no significant repellent effect against Culicoides was found for the citronella oil or the alpha-cyano-cypermethrin,
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while DEET had a significant repellent effect against Culicoides species and C. imicola for all catches made from after sunset to before sunrise (Page et al. 2009; see also Vente et al. 2014). Stuart et al. (2000) evaluated the repellent and antifeedant effect of derivatives
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of salicylic acid on the biting midge Culicoides impunctatus Goetghebeur. They noted that salicyluric acid strongly inhibited feeding. Following alkyl substitution of salicylic acid, it has been observed that o-thymotic and o-cresotic acids were also effective. Salicyluric acid indicated led to a marked protective effect in clinical trials; Stuart et al. (2000) hypothesized that this may result primarily from contact, since no repellent
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effects were achieved by salicyluric acid (Stuart et al. 2000).
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Later, González et al. (2014) studied the efficacy of 23 chemical and plantderived repellents against Culicoides obsoletus (Meigen) females, relying to Y-tube
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olfactometer assays. Therefore, the authors selected the ten most effective products for landing assay evaluation. The six most promising products were tested at 10% and 25%
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concentrations in field assays using the Centers for Disease Control (CDC) light traps. Notably, results varied according to the testing methodology. Indeed, while DEET at
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1 µg/µL was the most effective repellent in olfactometer assays, filter paper landing
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bioassays showed that plant essential oils, with special reference to lemon eucalyptus oil (see also Trigg 1996), achieved the best results, while light traps fitted with polyester mesh impregnated with a mixture of octanoic, decanoic and nonanoic fatty acids at 10% and 25% concentrations collected 2.2 and 3.6 times fewer midges than control traps, showing an efficacy comparable to DEET (González et al. 2014). While most of the researches on biting midge control targeted the adults, the control of young instar populations has been scarcely developed, since larval habitats of
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these vectors typically consisting of wet environments or frequent wet seeds livestock undertakings (Foxi and Delrio 2013; Zimmer et al. 2014). These larval development sites can be remediated with simple clearance operations carried out directly by the farmer, and industrial hygiene practices (Foxi et al. 2016). The larval populations could
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be also effectively managed relying to insecticides with low environmental impact. These new generation insecticides should be effective, readily soluble in water (without employing co-formulations and stabilizers), eco-friendly, with low risks for livestock and human health. They should be also selective against the targeted insect vectors. In this framework, natural product research can offer important innovations (Benelli et al.
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2017a).
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3. Neem products in the fight against arthropod vectors
Currently, a wide number of botanicals have been tested against arthropod
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vectors (Lorentz 2013, Benelli et al. 2014). Among them, a first-rank role is covered by neem (Azadirachta indica A. Juss.) (Benelli et al. 2015b). Neem is a tree of Indian
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origin belonging to the family of Meliaceae, whose products are gaining increasing
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importance in the context of natural insecticides (National Research Council 1992). The insecticidal properties of neem oil, mechanically extracted from the kernels containing the seeds, have been tested and certified by numerous institutions and by a wide scientific literature (Benelli et al. 2017a; see also Boeke et al. 2004).). Neem seeds contain more than 200 bioactive chemicals, even if attention has been mainly focused on limonoids (chemically known as nortriterpenes, e.g. azadirachtins, nimbin, nimbidin and nimbolides) (Nicoletti and Murugan 2013; Senthil-Nathan et al. 2005). The US
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Environmental Protection Agency (EPA) stated the insecticide efficacy and the absence of any environmental toxicity (Office of Pesticide Programs, and Biopesticides Pollution Prevention Diseases-Biopesticides Registration Document-Action Cold Pressed Neem Oil PC Code 025006). Neem is also the only plant-borne biocide
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accepted by the U.E. normative (Directive 2012/15/EU) (Benelli et al. 2017a). Notably, the extract of neem kernels has been used to control a wide array of arthropod pests and vectors (Mulla and Su 1999; Semmler et al. 2010; Nicoletti et al. 2016; Benelli et al. 2017a). Good examples include mosquitoes (Rao et al. 1992, 1995; Su and Mulla 1998a,b, 1999; Senthil-Nathan et al. 2005; Dua et al. 2009; Nicoletti et al.
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2010, 2012a,b; Mariani and Nicoletti 2013; Benelli et al. 2014; Benelli et al. 2015a),
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sandflies (Sharma and Dhiman 1993; Chandramohan et al. 2016), Ixodes and Rhipicephalus ticks, house dust mites, cockroaches (Blatta, Blattella and
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Gromphadorhina), raptor bugs (Triatoma), cat fleas, bed bugs (Schmahl et al. 2010), biting and bloodsucking lice (Al-Quraishy et al. 2011, 2012; Abdel-Ghaffar et al. 2012;
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Mehlhorn et al. 2012), Sarcoptes scabiei mites infesting dogs (Abdel-Ghaffar et al. 2008), poultry mites (Abdel-Ghaffar et al. 2009; Locher et al. 2010) and even beetle
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larvae feeding on poultry plumage (Walldorf et al. 2012). In addition, it has been also
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proved that neem cake, a cheap by-product of neem oil extraction, is also effective against insect pests and vectors (Benelli et al. 2014, 2015b).
4. Effectiveness of neem against Culicoides
The females of Culicoides, after mating in swarms and their blood meal, laid eggs (about 100-200) in muddy areas. The dark brown eggs are elongate and banana-
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shaped. The larvae are vermiform, without legs and prolegs, easy to recognize for eellike movements. The pupae are light brown with a pair of respiratory horns. The development from egg to adult usually takes about 15 -25 days, depending on climatic conditions (Figure 1).
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Larval populations of C. imicola develop mainly in muddy environments that are formed near drinking troughs and/or on artificial lakes edges used as water resources in livestock farms (Figure 2). The water quality in the larval habitats is characterized by a high concentration of organic matter derived from animal droppings. The larvae of C. imicola live in the surface layer of the soil, to a depth of several centimeters. In artificial
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ponds, larval foci are found in banks, in the first 50 cm above the water line (Foxi and
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Delrio, 2010). The larval stages of C. newsteadi, C. pulicaris and C. punctatus suit also live in drains, low brackish ponds and stream banks, often covered with herbs and rich
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in organic matter decomposition. On the other hand, the larvae of C. obsoletus and C. scoticus develop preferably in moist accumulations of leaves, in shaded environments in
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wooded areas and in the sheep manure heaps, horse and cattle in the fields (Delrio et al. 2002; Carpenter et al. 2008; Foxi et al. 2010).
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We focused on several experiments designed to control Culicoides larvae in
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field. In these experiments, a by-product from neem kernel oil extraction was employed, i.e. neem cake. This material is cheap, if compared to neem kernel oil, while retaining much of the chemical constitution (Nicoletti et al. 2010; Nicoletti et al. 2013), and then the toxic properties against targeted vectors (Benelli et al. 2015; Nicoletti et al. 2016). However, the potential usefulness of neem cake still should be still explored and fully validated in the field. In this scenario, the biology of Culicoides larvae offers us a perfect niche where the efficacy of neem cake-based products can be evaluated.
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In October 2008, the Department of Agriculture, University of Sassari, in collaboration with the Department of Environmental Biology, University of Rome "Sapienza" and C.R. ENEA Casaccia, in the frame of a research project funded by the Lazio Region, started aresearch to control Culicoides larvae in an extensive breeding of
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sheep in the province of Sassari (Sardinia, Italy), affected in previous years by outbreaks of bluetongue. In this study, a previous sampling revealed high populations of Culicoides larvae in a pond used for watering the animals. Therefore, a commercial product was employed, the Green Neem Cake (NeemGreen, Virudhunagar, India; i.e. neem cake granules), was tested against the larvae of Culicoides breeding in the open
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pond. In vitro tests were performed to establish a scale of efficacy of a series of
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fractions obtained throughout extraction of biphasic mixtures with decreasing polarity, extracted into ethyl acetate defatted neem cake (Nicoletti et al. 2010, 2012a,b). The field assays were carried out treating the shores of an artificial lake with
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Green Neem cake at 100 g/m2. A randomized complete block design with four
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replications of the treated and untreated plots was used (Foxi and Delrio 2013). The individual plots of an area of 1 m2 were contiguous to the shoreline for the length of 2 m
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and 50 cm wide. For the estimation of the population of Culicoides, from each single
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plot a mud sample of about 800 cm3 was collected. Each mud sample was scraped from the soil surface at 20 cm above shoreline using a flat trowel and maintained in laboratory for 30 days for retrieval of emerging biting midges. The samples were taken the week before the treatment, and then on a weekly basis for a month (Foxi and Delrio 2013). Results showed that the neem cake achieved a significant effect on the development of the Culicoides larvae (Table 1), with particular reference to C. imicola
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(Table 2), in agreement with previous studies that reported the neem oil ability to inhibit the oviposition of Culicoides, and act as ovicidal and larvicidal agent, along with a marked repellent activity (Blackwell et al. 2004; Narladkar et al. 2006). In the tests conducted, the commercial neem cake formulation showed a higher larvicidal
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effectiveness, if compared to the individual fractions. Notably, Foxi and Delrio (2013) showed that a single treatment with neem cake showed a considerable residual effect for about a month. The Green Neem Cake compared in the laboratory with other natural products such as commercial OIKOS 25 plus (azadirachtin A + B, 25%) showed superior efficacy (Foxi and Delrio 2013).
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Furthermore, besides larvicidal treatment against Culicoides young instars, it
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should be also pointed out that the neem oil has been also reported for its promising repellent and antifeedant activity against Culicoides adults, relying to three
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complementary methods with serial dilutions (Blackwell et al. 2004). Indeed, electroantennograms revealed the sensitivity of the females of Culicoides nubeculosus
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(Meigen) to neem oil ≥ 0.10%. Moreover, the females of Culicoides impunctatus Goetghebuer can be effectively repelled by ≥ 1% of neem oil in Y-tube olfactometer
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assays. Lastly, using a membrane feeder for wild-caught parous females of C.
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impunctatus, the proportion blood-feeding was significantly reduced by topical applications of neem oil ≥ 0.10% concentrations, with blood-feeding completely prevented by ≥ 1% (Blackwell et al. 2004). Based on these findings, Blackwell et al. (2004) proposed a neem-based formulation with 2% of neem oil for personal protection from Culicoides biting activity (see also Cole et al. 2002). However, personal protection tools have limited efficacy and high costs for prevention of bluetongue on livestock,
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where the treatment of young instar breeding sites remains the most appropriate control strategy in rural areas.
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5. Conclusions and challenges for future research
Overall, the neem oil and derived extraction products are already used in other countries in integrated control programs of insect pests and vectors (Su and Mulla 1999; Cole et al. 2002; Blackwell et al. 2004; Nicoletti et al. 2012; Foxi and Delrio 2013; Sujarwo et al. 2016; Benelli et al. 2015, 2017a). This article reviewed current control
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tools for the management of Culicoides larval and adult populations. Besides
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appropriate monitoring programs, as well as the use of repellents and antifeedant products against adults, we highlighted the concrete possibility of using neem cake for
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control of Culicoides young instar populations in wet environments close to livestock breeding sites. After the industrial process for the extraction of neem kernel oil, this by-
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product still contains relevant quantities of active metabolites (Nicoletti et al. 2012b, 2016). The above-discussed evidence of efficacy against Culicoides in the field
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represents the first attempt to use neem for larval control of the bluetongue disease
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vectors. Notably, this product is cheap and shows a considerable residual effect for a long period of time, about a month (Foxi and Delrio 2013). Furthermore, a better knowledge of Culicoides larval breeding sites is strategic
to establish an effective control of the vector species. Interventions to control Culicoides larvae integrated with adult insecticide treatments and use of eco-friendly repellents on livestock (Cole et al. 2002; Blackwell et al. 2004; Pavela et al. 2016) could provide a help to reduce the probability of transmission of bluetongue virus.
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The neem-borne products can also be used against adults Culicoides for systemic disinfection of animal housing and surrounding environments and as repellents with repeated treatments of the animals. Numerous studies report the multiple action of the constituents of the neem in the control of pests and vectors, according to multiple
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mechanisms of action (Del Serrone et al. 2015): interference with post-embryonic development by simulating the action of juvenoid substances that inhibits the metamorphosis and blocks the synthesis of ecdysone, phago-repellent action, and reduction of female oviposition rates and egg fertility (Semmler et al. 2010; Benelli et al. 2014, 2017a).
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Moreover, assuming a possible absorption through the skin, at the Research
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Centre for Animal Production of the Council for Research in Agriculture and Agricultural Economy Analysis tests have been conducted to evaluate the effect of
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neem on peripheral blood mononuclear cells of goats treated with neem and no adverse effects have been reported (De Matteis et al. 2015).
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For its highly effective and environmental care properties, neem kernel oil and neem cake have been ranked among the most interesting active substances for use in
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organic farming, with special reference to the control of insect pests and vectors
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(Blackwell et al. 2004; Benelli et al. 2017a). The neem is already used in other countries in IPM programs for the control of crop pests and management of livestock, as indicated by EPA in USA (EPA 2012). In Italy, although increasing, the use of neem is still limited and scarcely known, in comparison with the still large-scale employing of traditional pesticides. Based on the findings analyzed in this review, we believe that the employ of neem extraction by-products as aqueous formulation in muddy sites close to livestock grazing areas may represent a promising tool in the fight against the spread of
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bluetongue virus in the Mediterranean areas (Foxi and Delrio 2013). Therefore, we hope that the knowledge summarized here would boost research on eco-friendly control of Culicoides vectors, a One Health perspective integrating basic information on vector biology and ecology, phytochemistry, natural product research, and the employ of neem
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cake in the IPM framework, due to its high efficacy and multiple mechanisms of action.
Acknowledgements
The authors are grateful to Dr. Paolo Pasquali, Dr. Krisztian Magori and the
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anonymous reviewers for improving an earlier version of our manuscript.
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Conflict of Interest
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The Authors declare no competing interests.
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Figure 1. Life cycle of Culicoides imicola Kieffer (Diptera: Ceratopogonidae), a vector of the bluetongue virus and the African horse sickness virus.
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Female
I instar larva emerging from an egg
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Egg
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IV instar larva
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Figure 2. Main larval habitats of Culicoides imicola in Sardinia (Italy): muddy environments formed in proximity of livestock drinking troughs (a), as well as on artificial lakes edges (b)
(a)
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representing water resources for livestock farms.
(b)
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Table 1. Mean number (±SE) of Culicoides adults emerging from mud samples taken weekly in control and treated plots in Sassari (Sardinia, Italy) during October 2008. Within a column, means followed by the same letter are not significantly different
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(one-way repeated measures ANOVA, P=0.05) (Foxi and Delrio 2013).
Post-treatment
Treatment Pre-treatment 7 days Control
27.25±9.51 a
21 days
28 days
44.13±5.81 a 30.58±8.42 a 23.92±4.20 a 22.42±1.85 a 3.88±1.69 b
4.00±1.47 b
3.75±1.16 b
9.25±1.86 b
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Neem cake 17.63±3.56 a
14 days
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Table 2. Mean number (±SE) of C. cataneii, C. circumscriptus, C. festivipennis and C. imicola emerging during 4 weeks from mud samples in control and treated plots in Sassari (Sardinia, Italy) during October 2008. Within a column, means followed by the same letter are not significantly different (one-way repeated measures ANOVA,
C. cataneii
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P=0.05) (Foxi and Delrio 2013).
C. circumscriptus C. festivipennis
52.71±12.45 a
21.29±3.01 a
32.38±8.95 a
12.29±2.23 a
Neem cake
4.63±1.55 b
4.08±1.82 b
6.88±2.89 b
1.75±0.66 b
F1,6
28.27
16.58
6.52
36.59
P
0.0018
0.0066
0.0433
0.0009
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Control
C. imicola
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Graphical abstract
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Highlights
Bluetongue virus affects ruminants and is spread through the bites of Culicoides vectors
Effective vector control is crucial for prevention of bluetongue outbreaks
Culicoides larvae develop in muddy areas, their control is really challenging
Aqueous neem cake formulations in muddy sites represents a key tool to control
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bluetongue vectors
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In the field, residual efficacy of a single treatment with neem cake was >30 days
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