dc.description.abstract |
Rain-fed agriculture has affected African livelihood by making people vulnerable to climate-
related drought. Construction of dams and initiating irrigation schemes has therefore been widely
recognized as key solutions to ensure food security and enhance economic growth in drought prone
regions. In this regard, Ethiopia has embarked extensive dam constructions and irrigation
expansion to promote economic development. However, such development activities may cause
environmental modifications that could adversely affect the spread of vector-borne diseases such
as malaria. To date, there has been limited data evaluating the impact of environmental
modifications on the epidemiology of malaria and its vector bionomics.
Therefore, this study was done to evaluate impact of environment modifications on distribution
and ecology of malaria vector mosquitoes at Arjo-Dedessa Sugarcane Irrigation Scheme in
southwest Ethiopia. The study had three main objectives: i), it aimed to determine the existing
malaria transmission dynamics in the area (Chapter 4). ii), it aimed to identify breeding habitats of
malaria vector mosquitoes in the area (Chapter 5), and iii), it aimed to determine the effects of
change in the agroecosystem on survivorship and development of Anopheles gambiae s.l, the main
malaria vector in the area (Chapter 6).
Methods
Epidemiological and entomological surveys were conducted between 2017 and 2020 in Arjo-
Dedessa area of Southwestern Ethiopia. Retrospective data of malaria for the period between 2008
to 2017 were obtained from health facilities near the Arjo-Dedessa Sugarcane Irrigation area.
Malaria positivity rate, incidence rate, parasite species proportion, seasonality, age structure and
sex distribution were analysed and discussed (Chapter 4).
Entomological surveys were also conducted that encompasses; repeated cross-sectional survey for
Anopheles larval ecology study and life-table experiment for survivorship and development study.
Anopheles mosquito larvae were collected seasonally from two agroecosystems, ‘irrigated
sugarcane plantation’ (‘irrigated area’ hereafter) and ‘non-irrigated mixed crop-covered’ areas
(‘non-irrigated area’ hereafter) during the dry (December 2017 – February 2018) and wet (June
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2018 – August 2018) seasons. Mosquito habitat diversity and distribution, and larval abundance
were compared between the two agroecosystems and discussed (Chapter 5).
Life-table experiments were conducted to examine the effect of environmental modification on
survivorship of An. gambiae s.l both immatures and adults in irrigated and non-irrigated areas.
The pupation rate and development time of the immatures and adult longevity and fecundity were
compared between the two agroecosystems and discussed (Chapter 6).
Results
The epidemiological profile of malaria for the study area was mapped (Chapter 4). Over 10 years,
54,020 blood films were collected for malaria diagnosis in the health facilities at the area, of which
18,049 (33.4 %) were confirmed malaria cases by both microscopically and RDT. Plasmodium
falciparum, P. vivax, and mixed infection (P. falciparum and P. vivax) accounted for 8,660(48%),
7,649(42.4%), and 1,740(9.6%) of the malaria cases, respectively. The study also revealed that P.
vivax was the predominant over P. falciparum for four years (2010, 2014, 2015 and 2016). Malaria
has been reported in all age groups, but age distribution showed that the vast majority of cases
were adults above 15 years of age (73.7%). In all age groups, males were more significantly
affected than females. Moreover, malaria positivity rate showed a strong seasonality. However,
malaria cases were reported in all seasons across the 10 years data analyzed.
The association between environmental modification due to irrigated agriculture and Anopheles
mosquito larval habitat diversity and distribution, and larvae occurrence is discussed in Chapter 5.
In this study, 319 aquatic habitats were surveyed during the study period. Around 60% (n = 152)
of the habitats were positive for Anopheles mosquito larvae, of which 63.8% (n = 97) and 36.2%
(n = 55) were from irrigated and non-irrigated areas, respectively. The number of Anopheles
positive habitats was two-fold higher in irrigated than non-irrigated areas. Anopheles larval
abundance in the irrigated area was 16.6 % higher than in the non-irrigated area. Pearson’s chi-
square analysis showed that season, agroecosystem, and turbidity had a significant association with
larval Anopheles occurrence.
The effect of environmental modification on mosquito survivorship and development is discussed
in Chapter 6. The estimated mean survival time of female An. gambiae s.l in irrigated and non-
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irrigated area was 37.9 and 31.3 days, respectively. The estimated mean larval-to-adult
development time of An. gambiae s.l larvae was not found to be different in both irrigated and
non-irrigated areas. A survival analysis indicated that adult female An. gambiae s.l in the irrigated
area live significantly longer than those in the non-irrigated area. Females mosquitoes showed
higher longevity than males in both irrigated and non-irrigated areas.
Conclusions and recommendations
In general, malaria positivity showed a declining trend over 10 years period in the area. However,
in recent years of study, it showed a slight rise, which indicates that the area needs attention to
intensify the existing interventions to sustain control and enhance malaria elimination efforts.
This study found out a higher Anopheles mosquito breeding habitat diversity, larval occurrence
and abundance in the irrigated than non-irrigated areas in both the dry and wet seasons of the year.
This indicates that irrigation development activities contribute to the proliferation of suitable
mosquito breeding habitats that could increase the risk of malaria transmission. Incorporating
larval source management into routine malaria vector control strategies could help reduce
mosquito population density and malaria transmission around irrigation schemes.
Adult An. gambiae s.l survivorship was found to be enhanced in irrigated area than non-irrigated
area. Longer survival of adult mosquito in irrigated sugarcane plantation area may have important
implications in malaria transmission. Thus, routine monitoring of entomological indices and
environmental parameters in line with land use change is needed to detect any change in malaria
epidemiology and device toiler-made interventions |
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