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Dry Season Refugia Breeding Ecology of Mosquitoes (Diptera: Culicidae) in Minna, North Central Nigeria



I.K. Olayemi, B. Idris, I.C.J. Omalu and O.M. Odeyemi
 
ABSTRACT

This study was carried out in Minna, Nigeria, to elucidate the dry season breeding ecology of mosquitoes in the area thus, providing a basis for all-year-round effective implementation of informed larviciding interventions. Mosquito larvae were sampled bi-weekly between the hours of 0800 and 1100 from randomly selected larval breeding habitats in the city, using a 350 mL capacity Dipper. The physical characteristics of the selected habitats were evaluated and related to larval productivity. The results indicated that Anopheles mosquitoes constituted 55.00% of all larvae collected, followed by Culex (36.29%) and Aedes (17.49%). The patterns of mean monthly density distribution of the three mosquito Genera were similar, i.e., decreasing significantly (p<0.05) from the beginning to the end of the dry season. The mosquito types showed significant (p<0.05) preferences for certain habitats, with Anopheles and Aedes preferring the Drains (24.40±5.13 and 14.20±5.12 larvae/sampling day, respectively) and Culex mosquitoes encountered more frequently in the Swamps (16.80±6.22 larvae/sampling day). The Drains were the most productive habitats, accounting for over 50% larval production during the period, distantly followed by the Swamp (31.60±16.38 larvae/sampling day) while, the densities of larvae in the Wells and Rivers were significantly low (7.40±7.79 and 3.40±5.24 larvae/sampling day, respectively). Again, in terms of physical attributes, the Drains were the most ideal habitat for larval development, been relatively small (diameter = 2.30±0.00 m); most shallow (depth = 0.14±0.01 m); warmest (27.52±0.48°C) and nearest to human habitations (2.80±0.00 m). The epidemiological implications of these results were discussed and concluded that targeting dry season larviciding interventions at the productive larval breeding habitats will go a long way in reducing the menace of mosquito-borne diseases in Minna.

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I.K. Olayemi, B. Idris, I.C.J. Omalu and O.M. Odeyemi, 2012. Dry Season Refugia Breeding Ecology of Mosquitoes (Diptera: Culicidae) in Minna, North Central Nigeria. Journal of Biological Sciences, 12: 186-191.

DOI: 10.3923/jbs.2012.186.191

URL: https://scialert.net/abstract/?doi=jbs.2012.186.191
 
Received: November 28, 2011; Accepted: March 05, 2012; Published: June 12, 2012

INTRODUCTION

Mosquitoes are dipteran flies solely responsible for the transmission of important human diseases including malaria, filariasis, yellow fever, dengue fever, etc. (Belding, 1942; El-Badry and Al-Ali, 2010; Balakrishnan et al., 2011; Chakkaravarthy et al., 2011; Paulraj et al., 2011). These diseases have had serious negative impacts on the economic development, as well as, medical and social well-being of people living in their areas of prevalence (Amiruddin et al., 2012). For example, while dengue fever puts two-fifths of the world’s population at risk of infection, malaria accounts for 10% of Africa’s overall disease burden (Okenu, 1999; World Health Organization, 2003; Njan-Nloga et al., 2007) and kills about 300,000 Nigerians each year, especially pregnant women and young children below the age of five (Salako, 1997; Odaibo, 2006). The vectorial capacity of mosquitoes for the diseases they transmit is largely influenced by the intensity of larval production from breeding habitats (Depinay et al., 2004). Thus, the subject has received serious attention from mosquito (Anyanwu and Iwuala, 1999; Sogoba et al., 2007; Chaki et al., 2009) but such studies have focused mainly on the breeding of mosquitoes in the rainy season, due to the creation of abundant breeding habitats by rainfall; even though mosquitoes have adapted to breeding in large numbers in habitats that receive their moisture from sources other than rainfall.

To this end, though the level of mosquito breeding activities is significantly higher in the rainy than dry season (Olayemi and Ande, 2008), malaria prevalence rates remains relatively high in Minna during the dry season (Olayemi et al., 2009, 2012), indicating that the limited mosquito breeding activities in the dry season is above the threshold required for significant transmission of mosquito-borne diseases. Yet, mosquito larval control measures in Minna, as in other parts of Nigeria, are concentrated more in the rainy season against the back-drop that mosquito breeding in the dry season is inconsequential and may not promote the transmission of mosquito-borne diseases during this period thus, not deserving to be targeted for serious anti-larval mosquito control interventions. Thus, there is need for a systematic investigation of the breeding activities of mosquitoes during the dry season, so as to elucidate the active larval breeding sites during the period, a pre-requisite to the development of appropriate seasonally-sensitive mosquito anti-larval strategies. This study was, therefore, carried out to determine the relative densities and distribution of mosquito types in Minna during the dry season, assess the relative contributions of the larval breeding habitats to mosquito production in the area during this period, as well as, characterize such habitats.

MATERIALS AND METHODS

Study area: Minna, the capital city of Niger state, Nigeria, is located within longitude 6°33′E and latitude 9°37′N, covering an estimated land area of 88 km2, with an estimated human population of 1.2 million. The area has a tropical climate with mean annual temperature, relative humidity and rainfall of 30.20°C, 61.00% and 1334.00 mm, respectively. The climate presents two distinct seasons: a rainy season between May and October and a dry season (November-April). The vegetation in the area is typically grass dominated savannah with scattered tress.

Mosquito larval sampling, processing and identification: The city of Minna was searched for accessible dry season mosquito larval habitats (Fig. 1). Mosquito larvae were sampled bi-weekly from the habitats using a 350 mL capacity Dipper (Azari-Hamidian et al., 2011), between 0800 and 1100 h, from November 2008 to March 2009. Five samples were taken from each breeding site per sampling day. Collected specimens were immediately preserved in 40% formaldehyde solution and transported to the laboratory for further analysis. The larvae were identified to Genus level using aids provided by Hopkins (1952) and Gillies and Coetzee (1987).

Physical characterization of larval habitats: The distance between the larval habitats and the nearest human-inhabited house was measured in meters using a graduated tape.

Fig. 1: Map of Minna showing the sampling sites and habitat types 2 0 2 4 6 8 km, Source: Ministry of land and Survey, Minna, Niger State

The degree of exposure of larval habitats to sunlight was determined by estimating shade cover in percentages. The depth of water medium was measured using a meter rule while, the size of the surface area was determined by measuring the diameter along the widest plane. Water temperature was determined using an ordinary mercury thermometer, by dipping the bulb just below the water surface. Water turbidity was analysed electronically at the Quality Control Laboratory of Niger River Basin Development Authority, Minna.

Data analysis: Mosquito density was determined as mean number of larvae collected per sampling day and relative abundance of the Genera was expressed as simple percentages. Differences in larval densities of mosquito Genera in the various habitats, as well as, variations in the physical characteristics among the sites were compared using ANOVA. On the other hand, monthly variations in the densities of the mosquito Genera were compared using Chi-square test. All statistical differences were established at p = 0.05 level of significance.

RESULTS

Table 1 shows the mean relative abundance and monthly distribution of the mosquito Genera in Minna during the study period. The abundance of the mosquito types differed significantly (p< 0.05) with the anophelines constituting almost half of all larvae collected, distantly followed by Culex (36.29%) and Aedes (17.49%) mosquitoes. Aggregate mosquito density varied significantly (p<0.05) during the period, decreasing drastically from the beginning of the dry season (i.e., November = 28.20±9.80 larvae/sampling day) till March (11.00±4.00 larvae/sampling day). The mean monthly distribution of the individual mosquito Genus followed the same patterns as the aggregate population although, Aedes had its least density in February. During the five months study period, Anopheles had consistently significant (p<0.05) higher densities except during the month of December, when the genus was at par with Culex.

The larval habitat preferences of the mosquito Genera and relative productivity levels of the habitat types are shown in Table 2. Though, the three mosquito Genera were encountered in all the breeding sites investigated, they occurred at very low densities in some habitats. Anopheles and Culex showed significant preference for breeding in Drains and Swamps, respectively and were the dominant mosquitoes in these habitats. The Aedes mosquitoes bred preferentially in the Drains also (14.20±5.12 larvae/sampling day). The three Genera were more or less least encountered in the Rivers and Wells. The Drain was the most productive larval habitat during the study period, as more than 50% of the larvae were collected from this site, distantly followed by the Swamp (33.47%). Unlike the other two Genera, Anopheles was well represented in all four habitat types.

Table 3 shows the physical characteristics of the mosquito breeding habitats. The Wells and Drains were the nearest to human habitations while, the Swamp was the farthest (26.50±0.00 m). The breeding sites were mostly exposed to sunlight, ranging from 63.40±15.02% exposure in the Drains to almost 100% in the Wells. The depth of water in the breeding sites ranged from 0.14±0.01 m in Drains to 0.84±0.09 m in the Rivers. The River was the most turbid habitat (0.81±0.10 m) while the Well was the least (0.02±0.00 m). The surface area of the breeding sites were relatively large; while the Wells and Drains were the smallest, the Swamp had a mean diameter of 13.42±2.15 m and the River was the largest with mean 52.54±4.91 m surface area diameter.

Table 1: Mean monthly density of mosquito larvae in Minna, Nigeria, during the dry season of 2008/2009
*Values followed by same superscript alphabets in a row are not significantly different at p = 0.05, **Values in parenthesis are percentage distribution and such values followed by same superscript alphabets in the column are not significantly different at p= 0.05

Table 2: Mean density of mosquito larvae in different breeding habitats in Minna, Nigeria, during the dry season of 2008/2009
*Values followed by same superscript alphabets in a row are not significantly different at p = 0.05, **Values in parenthesis are percentage distribution, values followed by same superscript alphabets in the column are not significantly different at p = 0.05

Table 3: Mean physical parameters of different mosquito larval habitats in Minna, Nigeria, during the dry season of 2008/2009
*Values followed by same superscript alphabets in a column are not significantly different at p = 0.05

Water temperature varied within narrow limits (range = 25.50±0.77 to 27.52±0.48°C). However, while the Well was the coolest, the Drain was the warmest.

DISCUSSION

The three mosquito Genera namely, Aedes, Anopheles and Culex, that serve as vectors of serious human diseases including, yellow fever, malaria and filariasis, respectively, were encountered in Minna at fairly high densities though with drastic reductions in abundance as the dry season advanced. These results have important epidemiological implications for the transmission and control of mosquito-borne diseases in Minna. This may mean a high transmission rates of these diseases during the dry season, as earlier observed for malaria in the area (Olayemi et al., 2009), thus demanding a need for the intensification of anti-larval interventions during the dry season. Such efforts will yield encouraging results, as fewer sites will be targeted for larviciding measures, coupled with the fact that the population density of the mosquitoes is already undergoing drastic reductions, probably, due to the effects of inclement weather conditions characteristic of the dry season.

The mosquito types showed significant preferences for breeding in certain habitats, results similar to those reported from Ilorin, a neighbouring State Capital (Olayemi and Ande, 2008; Olayemi et al., 2011). Studies have shown that mosquitoes possess distinct oviposition attractants in the form of the presence of certain salts, conspecific organisms, aquatic vegetation and/or absence of certain predators in larval habitats thus, determining their density in such sites (Hwang et al., 1980; Bentley and Day, 1989). While, the breeding site preferences exhibited by the Anopheles and Culex mosquitoes, i.e., Drains and Swamps, respectively, agree with the results of similar studies elsewhere (Goma, 1960; Olayemi and Ande, 2008), that of Aedes, i.e. Drains, contradicted the known breeding habit of the Genus. Ae. aegypti, for example, breeds preferentially in domestic containers around homes (Adebote et al., 2006; Brown et al., 1992). Therefore, the preference of Aedes mosquitoes for breeding in the Drains during the dry season in Minna, may be due to the usual scarcity of water-holding domestic containers during such period and confirms the adaptability of Ae. aegypti, for example, to breeding in large numbers in unusual habitats when preferred conventional sites are not available.

The Drains were the most productive larval habitats during the dry season in Minna. The reasons for this finding may not be far-fetched as; incidentally, certain physical characteristics of this habitat type make it ideal for high mosquito larval production. To this end, the Drains were the smallest/most shallow and warmest habitats during the period. While, the former attributes will ensure the absence of large predators (Lundkvist et al., 2003), the latter promotes high metabolic rates and hence faster larval survival and developmental rates (Kirby and Lindsay, 2009). Thus, coupled with the fact that the Drains were the nearest mosquito breeding sites to homes, this habitat type pose serious threats to the health of the residents of Minna, as the high mosquito production from these sites will ensure intense human-vector contact and hence, transmission of mosquito-borne diseases. The Wells and Rivers in Minna were not active mosquito production sites during the dry season. This may be due to the presence of large predators and low temperature in the Rivers and small surface area exposed to atmospheric oxygen and constant disturbance caused by the dipping of water-fetching buckets into the Wells.

CONCLUSION

Mosquito vectors of diseases bred actively but preferentially in certain larval habitats during the dry season in Minna, confirming the relatively high prevalence rates of mosquito-borne diseases in the area during this season; thus, suggesting the need for the intensification of anti-larval measures even in the dry season. The Drains posed the greatest threat to the health of the residents of Minna, been the most productive mosquito breeding sites in the dry season, occasioned by their favourable environmental conditions for the survival and faster developmental rates of larvae. Therefore, targeting dry season larviciding measures at such preferred and productive breeding sites will go a long way in reducing the menace of mosquito-borne diseases.

REFERENCES
Adebote, A.D., J.S. Oniye, S.I. Ndams and K.M. Nache, 2006. The breeding of mosquitoes (Diptera: Culicidae) in peridomestic containers and implication in yellow fever transmission in villages around Zaria, Northern Nigeria. J. Entomol., 3: 180-188.
CrossRef  |  Direct Link  |  

Amiruddin, R., D. Sidik, A. Alwi, N. Islam, Jumriani, P. Astuti and Syafruddin, 2012. Socioeconomic factors and access to health services for malaria control in Mamuju District, West Sulawesi Indonesia. Asian J. Epidemiol., 5: 56-61.
CrossRef  |  

Anyanwu, G.I. and M.O.E. Iwuala, 1999. Mosquito breeding sites: distribution and relative abundance of species in the Jos Plateau, Nigeria. Med. Entomol Zool., 50: 243-249.

Azari-Hamidian, S., M.R. Abai, K. Arzamani, H. Bakhshi, H. Karami, H. Ladonni and R.E. Harbach, 2011. Mosquitoes (Diptera: Culicidae) of North Khorasan province, Northeastern Iran and the zoogeographic affinities of the Iranian and middle Asian mosquito fauna. J. Entomol., 8: 204-217.
CrossRef  |  Direct Link  |  

Balakrishnan, S., M. Srinivasan and K. Elumalai, 2011. A survey on mosquitoe diversity in parangipettai coast, Southeast coast of Tamilnadu, India. J. Entomol., 8: 259-266.
CrossRef  |  Direct Link  |  

Belding, D.A., 1942. extbook of Clinical Parasitology. Appleton-Century-Crfts Inc., New York, USA., pp: 317.

Bentley, M.D. and J.F. Day, 1989. Chemical ecology and behavioral aspects of mosquito oviposition. Annu. Rev. Entomol., 34: 401-421.
CrossRef  |  

Brown, M.D., P. Mottram, I.D. Fanning and B.H. Kay, 1992. The peridomestic container-breeding mosquito fauna of Darnley Is. (Torres Strait) (Diptera:Culicidae), and the potential for its control by predacious Mesocyclops copepods. Austr. J. Entomol., 31: 305-310.
CrossRef  |  

Chaki, P.P., N.J. Govella, B. Shoo, A. Hemed, M. Tanner, U. Fillinger and G.F. Killeen, 2009. Achieving high coverage of larval-stage mosquito surveillance: challenges for a community-based mosquito control programme in urban Dar es Salaam, Tanzania. Malar. J., Vol. 8. 10.1186/1475-2875-8-311

Chakkaravarthy, V.M., T. Ambrose, S. Vincent, R. Arunachalam, M.G. Paulraj, S. Ignacimuthu and G. Annadurai, 2011. Bioefficacy of Azadirachta indica (A. juss) and Datura metel (Linn.) leaves extracts in controlling Culex quinquefasciatus (Diptera: Culicidae). J. Entomol., 8: 191-197.
CrossRef  |  Direct Link  |  

Depinay, J.O., C.M. Mbogo, G. Killeen, B.J. Knols and J. Carlson et al., 2004. A simulation model of African Anopheles ecology and population dynamics for the analysis of malaria transmission. Malar. J., Vol. 3. 10.1186/1475-2875-3-29

El-Badry, A.A. and K.H. Al-Ali, 2010. Prevalence and seasonal distribution of dengue mosquito, Aedes aegypti (Diptera: Culicidae) in Al-Madinah Al-Munawwarah, Saudi Arabia. J. Entomol., 7: 80-88.
CrossRef  |  Direct Link  |  

Gillies, M.T. and M. Coetzee, 1987. Supplement to the Anophelinae of Africa, South of the Sahara (Afrotropical region). Publication S. Afr. Inst. Med. Res., 55: 1-143.
Direct Link  |  

Goma, L.K.H., 1960. The swamp-breeding mosquitoes of Uganda: records of larvae and their habitats. Bull. Entomol. Res., 51: 77-94.
CrossRef  |  Direct Link  |  

Hopkins, G.H.E., 1952. Mosquitoes of Ethiopian Region: Larval Bionomics of Mosquitoes and Taxonomy of Culicine Larvae. 2nd Edn., Adlard and Sons Ltd., London.

Hwang, Y.S., W.L. Kramer and M.S. Mulla, 1980. Oviposition attractants and repellents of mosquitoes. J. Chem. Ecol., 6: 71-80.
CrossRef  |  

Kirby, M.J. and S.W. Lindsay, 2009. Effect of temperature and inter-specific competition on the development and survival of Anopheles gambiae sensu stricto and An. Arabiensis larvae. Acta Trop., 109: 118-123.
PubMed  |  

Lundkvist, E., J. Landin, M. Jackson and C. Svensson, 2003. Diving beetles (Dytiscidae) as predators of mosquito larvae (Culicidae) in field experiments and in laboratory tests of prey preference. Bull. Entomol. Res., 93: 219-226.
CrossRef  |  

Njan Nloga, A.M., P. Saotoing, J.C. Tchouankeu and J. Messi, 2007. Effect of essential oils of six local plants used insecticide on adults of Anopheles gambiae, Giles 1902. J. Entomol., 4: 444-450.
CrossRef  |  Direct Link  |  

Odaibo, F.S., 2006. Malaria scourge: The facts, the lies and the politics. http://www.gamji.com/article5000/NEWS5145.htm.

Okenu, D.M.N., 1999. An integrated approach for malaria control in Africa. Malar. Infect. Dis. Afr., 10: 4-13.
Direct Link  |  

Olayemi, I.K. and A.T. Ande, 2008. Species composition and larval habitats of mosquitoes (Diptera: Culicidae) in Ilorin, Nigeria. Zoologist, 6: 7-15.

Olayemi, I.K., A.T. Ande, A.V. Ayanwale, A.Z. Mohammed and I.M. Bello et al., 2011. Seasonal trends in epidemiological and entomological profiles of Malaria transmission in North Central Nigeria. Pak. J. Biol. Sci., 14: 293-299.
CrossRef  |  Direct Link  |  

Olayemi, I.K., A.T. Ande, B. Isah and A.R. Idris, 2009. Epidemiology of malaria in relation to climatic variables in Minna, Nigeria. Afr. J. Med. Sci., 2: 5-10.

Olayemi, I.K., I.C.J. Omalu, S.O. Abolarinwa, O.M. Mustapha and V.A. Ayanwale et al., 2012. Knowledge of malaria and implications for control in an endemic urban area of north central Nigeria. Asian J. Epidemiol., 5: 42-49.
CrossRef  |  

Paulraj, M.G., A.D. Reegan and S. Ignacimuthu, 2011. Toxicity of benzaldehyde and propionic acid against immature and adult stages of Aedes aegypti (Linn.) and Culex quinquefasciatus (Say) (Diptera: Culicidae). J. Entomol., 8: 539-547.
Direct Link  |  

Salako, l., 1997. Malaria the Unending Saga. Keynote Address. In: Coping with Treatment Failures in Malaria, Obi, C.C. (Ed.). Mayer and Baker, Lagos, pp: 13-25.

Sogoba, N., S. Doumbia, P. Vounatsou, I. Baber and M. Keita et al., 2007. Monitoring of larval habitats and mosquito densities in the Sudan savanna of Mali: Implications for malaria vector control. Am. J. Trop. Med. Hygiene, 77: 82-88.
PubMed  |  

World Health Organization, 2003. The Africa malaria report, Geneva. World Health Organization.

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