Ecology and Infection Status of Sand Flies in Rural and Urban Cutaneous Leishmaniasis Endemic Areas in Northwest Ethiopia
by
, , , and
Wondmeneh Jemberie
1,2,*,
Abebe Animut
1,
Sisay Dugassa
1,
Araya Gebresilassie
3,
Roma Melkamu
4,
Esayas Aklilu
1,
Mulugeta Aemero
5,
Johan van Griensven
6 and
Myrthe Pareyn
6 1
Vector Biology & Control Research Unit, Aklilu Lemma Institute of Pathobiology, Addis Ababa University, Addis Ababa P.O. Box 1176, Ethiopia
2
Department of Biology, College of Natural and Computational Sciences, University of Gondar, Gondar P.O. Box 196, Ethiopia
3
Department of Zoological Sciences, College of Natural and Computational Sciences, Addis Ababa University, Addis Ababa P.O. Box 1176, Ethiopia
4
Leishmania Research and Treatment Center, University of Gondar, Gondar P.O. Box 196, Ethiopia
5
Department of Medical Parasitology, School of Biomedical & Laboratory Sciences, College of Medicine & Health Sciences, University of Gondar, Gondar P.O. Box 196, Ethiopia
6
Clinical Sciences Department, Institute of Tropical Medicine Antwerp, 2000 Antwerp, Belgium
*
Author to whom correspondence should be addressed.
Trop. Med. Infect. Dis. 2024, 9(3), 52; https://doi.org/10.3390/tropicalmed9030052
Submission received: 26 November 2023
/
Revised: 30 January 2024
/
Accepted: 31 January 2024
/
Published: 23 February 2024
(This article belongs to the Special Issue Leishmaniasis: Vector-Host-Pathogen Interactions in Health and Disease)
Abstract
:Cutaneous leishmaniasis (CL) caused by Leishmania aethiopica is transmitted by Phlebotomus longipes in northern Ethiopia. No studies have been conducted to investigate the transmission dynamics of CL, despite its high endemicity in both rural and urban settings. Evidence on the ecology and behavior of the vector from this area are required to develop integrated disease control strategies. Sand flies were collected in the dry and wet seasons in 2021 in CL-endemic rural Gindmeteaye and urban Addis-Alem in northwest Ethiopia. Trapping was performed with sticky and Centers for Disease Control and Prevention (CDC) light traps in three habitats, including inside patients’ houses, peridomestic areasand in caves/rocky areas. Sand flies were morphologically identified to species level. Female Phlebotomus species were categorized according to blood feeding status and tested by spliced-leader (SL-) ribonucleic acid (RNA) polymerase chain reaction (PCR) to screen for Leishmania infection. Of 1161 sand flies, the majority (77%) were P. longipes, six (0.5%) were P. orientalis and the remaining were Sergentomyia. The abundance of the 430 female P. longipes was significantly linked to seasonality (p < 0.001), with the majority in the dry season occurring in the outdoor rocky (37%) and peridomestic (34%) sites, while, in the wet season, most (62%) were captured indoors. This seasonality was more pronounced in rural Gindmeteaye, where housing construction is poor. The number of blood-fed and gravid P. longipes was significantly higher in the wet (31%; 22%), compared to the dry season (13%; 8%), and their proportion was highest indoors. Eighteen (4%) female P. longipes were Leishmania positive, with highest infection prevalence in caves (7% compared to 3% indoors, p = 0.022), and in the dry season (6%, p < 0.001). Phlebotomus orientalis specimens were all captured in May in rural Gindmeteaye, five indoors and one in a peridomestic site. Further research should be conducted to investigate the absolute contribution of humans and indoor transmission to the transmission cycle of CL. Inhabitants of endemic villages should be made aware that evening outdoor activities near caves may increase their exposure to infectious sand flies. Whether P. orientalis can breed and become infected at high altitudes should be further studied.
1. Background
A bite of a Leishmania-infected female phlebotomine sand fly vector can cause cutaneous leishmaniasis (CL). CL is a skin disease that manifests in lesions which predominantly occur on patients’ face and extremities and leave disfiguring scars after healing. It is the most common neglected tropical diseases (NTDs) involving the skin in Ethiopia, with a yearly estimate of 20,000 to 50,000 cases, although less than 800 were reported to WHO in 2021 [1,2]. The disease occurs on the slopes of the Ethiopian Great Rift Valley spanning from northwest to southwest and from south to east of the country, at altitudes ranging between 1600 and 2700 m [3]. Although there are a few well-described hotspots of CL [4,5,6,7,8], endemic areas are highly underreported and the distribution is more widespread than previously described.
Cutaneous leishmaniasis in Ethiopia, and some parts of Kenya, is mainly caused by Leishmania aethiopica, although a recent study in northern Ethiopia showed a few CL causes caused by L. donovani [9]. CL caused by L. aethiopica is generally severe and manifests in three forms: localized CL (LCL), mucocutaneous leishmaniasis (MCL) and diffuse cutaneous leishmaniasis (DCL).
The principal animal reservoirs for L. aethiopica are hyraxes (Heterohyrax brucei and Procavia capensis), which are abundant in rocky areas and caves [10]. Infection prevalence in these animals was found to be up to 20% [4,6]. Humans are also proven to efficiently transmit L. aethiopica to the vector [11]. Phlebotomus (Larroussius) longipes and P. (La.) pedifer have been identified as the main vectors of L. aethiopica in the north and south of the country, respectively [6]. Their breeding sites are rocky areas, caves, stony fences surrounding houses, gorges and tree cavities, where sand fly larvae feed on fecal materials of hyraxes [6,12,13]. In southern and central Ethiopia, research on the behavior of the vector has shown that their blood meal sources were mainly derived from humans, hyraxes and livestock, although the latter have never been found infected with Leishmania parasites. The vectors were demonstrated to be predominantly endophagic and mainly active around midnight [7,14].
The ecology and behavior of a vector are highly dependent on climate, topography and other environmental factors, which are different in northwestern Ethiopia compared to the center and south of the country. Yet, most information about the vector’s abundance, ecology and behavior originates from the latter two, questioning whether this can be generalized to the northwest, where transmission studies in CL endemic areas are scarce.
Patient records from the Leishmaniasis Research and Treatment Center (LRTC) in Gondar, northwest Ethiopia, demonstrate that there are many CL cases coming from both Gondar city and rural areas in the surroundings. There is no knowledge yet on how the transmission dynamics in the north and south or in urban and rural areas differ from each other, which should be properly investigated in order to design integrated vector control measures.
In this study, we assessed the spatial and temporal distribution of (infected) sand flies in an urban and rural endemic area of CL in northwestern Ethiopia. The findings will contribute to a better understanding of the disease’s transmission dynamics and design of control measures.
2. Methods
2.1. Description of Study Sites
This study was conducted in two sites that are known to be endemic of CL, based on the records of the LRTC in Gondar: an urban village, Addis-Alem, in Gondar city and a rural village, Gindmeteaye, in Lay-Armachiho woreda (district). Both are situated in the Amhara region in northwest Ethiopia, where Gondar is one of the major cities (Figure 1).
Addis-Alem is located at an elevation of approximately 2100 m at the border of Gondar city. It is an urban area, with a rocky cliff with hyraxes situated at one end of the village, nearby a mosque where people go to pray, also at night. Gindmeteaye lies at an elevation of about 2400 m at 29 km from Gondar. It is a rural area, mostly covered by farmland, where hyraxes and rocky areas are abundant throughout the village.
In both villages, household compounds are surrounded by stony fences with crevices in between. The study sites have a similar climate, with an annual rainfall of about 200–600 mm per year. The rainy season starts in May until the end of September and has cool temperatures ranging between 18 and 22 °C. In the dry season, from October to April, the temperature is generally higher, ranging from 22 to 28 °C.
2.2. Sand Fly Collections
Sand flies were collected during the dry season in February, March and April 2021 and during the wet season in May, July and August 2021 in both rural and urban villages. Each month, trapping was performed for five consecutive nights in the two study sites. In every village, six trapping sites were employed in three habitats; two indoors in houses of patients with active CL at the start of the study (identified by a physician), two peridomestic places outside a CL patient’s house and two in caves or rocky areas where hyraxes resided. In each collection site, trapping was carried out using one standard CDC miniature light trap (John W. Hock Company, Grainesville, FL, USA; supplementary file: Table S1) set-up at 0.5 to 1 m above the ground, and five A4-format laminated sticky traps covered with sesame oil on both sides, placed against walls or within rock crevices. Traps were set-up at dusk and collected at dawn (Figure 2). The employed collection methods did not affect the environment. Collected sandflies were sorted and stored in absolute ethanol at −20 °C until further processing.
2.3. Sandfly Dissection and Morphological Identification
After collection, sand flies were sorted under the stereomicroscope according to sex, genus (Phlebotomus or Sergentomyia) and engorgement status (unfed/sugar fed, blood fed or gravid). Subsequently, the head and last segments of the abdomen were dissected and used for mounting in CMCP-10 high viscosity mountant (Polysciences, Hirschberg, Germany). All mounted sand flies were identified to species level using relevant morphological keys [17,18,19,20,21]. The thorax and remaining part of the abdomen were individually stored again in absolute ethanol at −20 °C for molecular analysis.
2.4. Leishmania Detection in Sandflies
All female Phlebotomus sand flies were molecularly screened for Leishmania parasites. Nucleic acid isolation of the individual sand flies’ thorax and abdomen was performed using a crude, in-house prepared extraction buffer, as described previously [13]. In each extraction batch of 22 samples, two negative extraction controls (lysis buffer only) and a positive extraction control (Lutzomyia longipalpis, laboratory-infected with Leishmania major) were added to check for contamination and extraction efficiency. Extracts were diluted with nuclease-free water, after which they were subjected to a PCR, targeting the 39 bp spliced-leader RNA (SL-RNA) gene, as described previously [22]. In each run, two positive PCR controls, two non-template controls and the extraction controls were added to assess the validity of the extraction and PCR run. Amplification was performed using the QuantStudio5 Real-Time PCR System (Applied Biosystems, ThermoFisher Scientific, Merelbeke, Belgium). Samples were considered positive if they had a cycle threshold value < 35 and a melting temperature (Tm) less than 0.5 °C different from the average Tm of the positive controls. The P. longipes specimens positive for SL-RNA were subjected to a PCR targeting the ITS-1 gene followed by a high resolution melt (HRM) curve analysis to determine the species of Leishmania. The assay was performed as described previously [23] and run on a Rotor Gene Q instrument (Qiagen, Antwerp, Belgium), including the DNA of cultivated Leishmania species as controls (L. aethiopica MHOM/ET/72/L127, L. tropica MHOM/PS/2003/LRC-L1022, and L. donovani MHOM/SD/2007/Ged4).
2.5. Data Analysis
Statistical analysis was performed in R Studio version 4.1.3 [24]. Chi-squares tests were employed to compare the sand fly abundance and blood feeding status between habitats, seasons and study sites. Binomial tests were used compare the difference in infection rate of P. longipes between habitats, seasons and study sites. The level of significance was p < 0.05.
3. Results
3.1. Species Typing
A total of 1161 sand flies were caught in the two study sites combined (Table 1), of which 838 (72%) were trapped with CDC light traps and the remaining 323 with sticky traps. Overall, 256 specimens (22%) belonged to the Sergentomyia genus and 905 (78%) were Phlebotomus. Among the Sergentomyia, we identified 156 (13%) S. schwetzi, 77 (7%) S. clydei and 23 (2%) S. adleri. Two species of Phlebotomus were identified, including 899 (77%) P. longipes and 6 P. orientalis. About half (430/899, 48%) of the P. longipes and two out of six P. orientalis were female. While the proportion of P. longipes captures in the rural and urban villages were similar, all P. orientalis sand flies were captured in the rural Gindmeteaye village.
3.2. Spatio-Temporal Sandfly Abundance
Of the 430 female P. longipes sand flies, 254 (59%) were found in the dry and 176 (41%) in the wet season (Table 2). Preference for habitats was significantly linked to seasonality (p < 0.001). While in the dry months, more (p < 0.001) sand flies were captured in outdoor habitats like rocky areas (37%) and peridomestic areas (34%), in the wet season, the majority (p = 0.001) of the female P. longipes sand flies were captured indoors (62%), with only 28% found in peridomestic are and 10% in rocky areas and caves. This seasonality in habitat preference was similar in both sites, with 63% of the female P. longipes and flies residing inside houses in the wet season in rural Gindmeteaye and 60% in urban Addis-Alem. Four male and one female P. orientalis were all captured inside case houses, and one specimen was collected in a peridomestic habitat. All six were found at the start of the rainy season in May.
3.3. Spatio-Temporal Variation in Sandfly Physiological Status
Among the 430 female P. longipes, 88 (20%) were blood-fed, 59 (14%) gravid and the remaining 283 (66%) were either sugar- or non-fed (Table 3). The proportion of blood-fed and gravid sand flies was higher in rural Gindmeteaye (28% and 18%, respectively) than in urban Addis-Alem, where 13% of the P. longipes specimens were blood-fed and 10% were gravid (Table 4). The number of blood-fed specimens was significantly higher in the wet (55/176, 31%) compared to the dry season (33/254, 13%, p < 0.001, Table 3). Likewise, significantly more gravid sand flies were found in the wet (38/176, 22%) than the dry season (21/254, 8%, p < 0.001). This trend was similar for all three habitats. The proportions of blood-fed and gravid sand flies were highest indoors, with 24% (44/182) and 16% (29/182), respectively, followed by 19% and 13% in peridomestic areas and 16% and 11% in caves/rocky areas, although these differences were not significant (p = 0.235 for blood-fed and p = 0.463 for gravid). Of the two P. orientalis female sand flies, the specimen found inside the CL case house was blood-fed; the other one was non-fed.
3.4. Leishmania Infection
Of the 430 individual P. longipes sand flies tested by PCR for Leishmania, 18 (4%) were positive (Table 4). The species of Leishmania could not be successfully determined. Infection prevalence was significantly lower (p = 0.005) in rural Gindmeteaye with 2% (4/202), compared to 6% (14/228) in urban Addis-Alem. The proportion of infected P. longipes was highest in caves, where eight out of 110 (7%, p = 0.022) were positive for Leishmania, followed by 4% (5/138) for peridomestic areas and 3% (5/182) indoors. The proportion of infected sand flies was higher in the dry (6%, p < 0.001) than the wet (2%) season. Ten of the positive sand flies were non-fed, five were blood-fed and three were gravid. The two female P. orientalis sand flies were both negative for Leishmania PCR.
4. Discussion
Our study is the first eco-epidemiological study investigating the transmission of CL in northwest Ethiopia. We demonstrate that transmission is ongoing in urban Addis-Alem, in the suburbs of Gondar city, which lies at the very suitable altitude, for P. longipes, of 2100 m and has caves and stony fences around houses. While most known hotspots of CL are described to be in rural areas, another study showed that CL in Ethiopia occurs in the areas surrounding Addis Ababa, where a cliff and hyraxes are present, indicating the importance of the animal reservoir [4]. Based on records from the LRTC in Gondar, cases are indeed also coming from Gondar city. Future studies should investigate whether infected sand flies also occur more towards the center of the city, where hyraxes are not present to determine what the role of human hosts in the transmission cycle is when the animal reservoir is not present.
Majority of the sand flies in our study were P. longipes, which corresponds with previous entomological research conducted in Gondar and Lay-Armachiho (the district in which Gindmeteaye village is situated). However, these authors also collected three P. gibiensis specimens in both sites [25], which were not found in our study.
Similar to findings from southern Ethiopia, most female P. longipes in urban Addis-Alem were captured in the dry season [13]. However, in rural Gindmeteaye, P. longipes was most abundant in the wet season. This could be because sand flies were predominantly found indoors here, whereas, in urban Addis-Alem, the abundance was more equal throughout the different habitats. Although no objective records are available from our study, field observations indicate that housing structures in urban Addis-Alem were better than in rural Gindmeteaye, where there were more gaps and cracks in the walls and roof. The better housing structures could potentially have prevented sand flies from entering the houses for feeding and resting [26]. For malaria, improving housing structures and screening doors and windows was proven effective at protecting humans from indoor mosquito vector bites and reducing their risk of infection [27]. More data are needed to objectively investigate whether improved housing structures are related to lower numbers of indoor sand fly vectors, to determine whether screening could also be an effective control measure for endophilic sand fly vectors.
More female P. longipes were captured indoors in the wet compared to the dry season in both sites, indicating that the vector seeks shelter indoors when it is rainy. This important finding could not be demonstrated in the south, where sand fly collection was not performed indoors, leading to a biased low abundance of sand flies in the wet season [13]. Possibly, if indoor collections would have been performed in that study, P. pedifer would have been more abundant indoor in the wet season as well. This indicates that, potentially, vector control strategies should be different in the wet and dry season. Importantly, the proportion of blood-fed sand flies was found to be the highest indoors, indicating the potential for indoor transmission, as was previously described in the south, where most blood-fed sand flies were found indoors and fed on humans. However, blood meal sources were not determined in our study and could be different from the south. Likewise, the proportion of gravid sand flies was highest indoors, which could indicate that the vector is also breeding indoors or in peridomestic areas, in which case the dung of livestock could serve as a breeding site. The presence of animal dung inside household compounds was recently identified as a risk factor for CL (manuscript in preparation). Hence, further research is required to determine whether sand flies can breed in animal dung, which can be determined based on the rotation of genitalia of male sand flies [28].
The overall Leishmania infection prevalence of P. longipes in our study was 4%, which is in line with findings from other endemic sites in the country. Infection rates were highest in urban Addis-Alem, despite the fact that, based on hospital records, more patients come from Gindmeteaye. Additionally despite the fact that most blood-fed and gravid sand flies were found inside houses, most infected P. longipes were found in caves. This is in line with previous findings from southern Ethiopia, where significantly more infected sand flies were found in caves [7,13].
In contrast to the proportion of blood-fed and gravid sand flies, which was found to be highest indoors in the wet season, the proportion of infected sand flies was highest in the dry season, when sand flies are mostly found in caves and peridomestic habitats, confirming that hyraxes play an important role in transmission [4,6,13,29]. This also corresponds with risk factor studies indicating that undertaking outdoor activities (e.g., fetching water or wood and herding animals) near hyrax habitats or caves in particular is a significant risk factor (manuscript in preparation). Hence, communities should be made aware of the risks of such activities after dusk.
Overall, more evidence is required on the absolute contributions of hyraxes and humans to the transmission of CL in both seasons. Furthermore, it should be investigated whether humans have the highest risk of infection inside their dwellings or during outdoor activities near caves. This would enable the design of effective integrated control measures for the control of CL in northwest Ethiopia.
Besides P. longipes, we also found P. orientalis in rural Gindmeteaye. Phlebotomus orientalis is the vector for L. donovani, causing visceral leishmaniasis (VL) in northwest Ethiopia and Sudan. It commonly occurs in the lowlands where temperatures are high, and its presence is associated with habitats like vertisols, Acacia and Balanites trees [30]. Our study reports the highest elevation (2400 m) from which P. orientalis has ever been collected, with previous records at high altitudes of 1800 m in Addis Zemen [31] and 2000 m in Libo-Kemekem [32,33] in Ethiopia. The P. orientalis specimens in our study were captured in May, which is the hottest month of the year in the study area, yet the typical habitats are not present in Gindmeteaye. Five out of six specimens were found indoors. Although only few specimens were captured, a potential explanation of this species occurring at such high altitude could be climate change, allowing the species to survive here in the hottest months but indoors only. Such changes can result in the altered behavior of the vector as it adapts to new climatic conditions. Further studies need to explore whether the species can breed and become infected at high elevations, as that could have a huge impact on immunologically naive populations, potentially leading to outbreaks of VL. There are some confirmed VL cases presenting at the LRTC in Gondar who do not have any travel history to lowland areas where the disease is endemic. This is currently being further investigated. Moreover, recent evidence indicates that CL caused by L. donovani occurs in Ethiopia as well [9], although no whole genome sequencing was performed to assess whether this could have been a hybrid between L. donovani and L. aethiopica. This hybridization could have occurred in the midgut of P. orientalis [34,35]. One should further investigate whether P. orientalis is a permissive vector and could potentially lead to the formation of hybrid species, which could be a threat to public health in Ethiopia and beyond.
In this study, we trapped sand flies in both the wet and dry season, in indoor and outdoor habitats. The limitations are that we did not isolate the Leishmania parasites or determine the Leishmania species and blood meal sources of the sand flies. Such information would be valuable to further investigate which hosts play an important role in transmission. Moreover, information on the weather conditions (temperature, rain fall) and housing structures is lacking, so the hypothesis that good housing structures could potentially prevent sand flies from entering houses cannot objectively be substantiated. Generally, a follow-up study in the region should employ a One Health approach, so that a holistic overview of the situation can provide the necessary insights to develop a successful control program for CL.
5. Conclusions
This eco-epidemiological investigation in CL-endemic rural Gindmeteaye and urban Addis-Alem in northwest Ethiopia revealed that P. longipes was mostly found outdoors, in caves and peridomestic ecotypes, in the dry season. Likewise, Leishmania prevalence in P. longipes was highest in the dry season, in caves. On the contrary, in the wet season, most blood-fed and gravid sand flies were captured indoors, with a lower proportion infected. Further research is required to investigate the absolute contribution of humans and hyraxes to the CL transmission cycle and determine whether the highest risk of infection is indoors or outdoors. Furthermore, we showed that P. orientalis occurred in CL-endemic areas, although in low numbers. It should be investigated whether they can breed and become infectious as such high altitudes, and whether they are permissive vectors, which could potentially lead to the formation of hybrid species.
Supplementary Materials
The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/tropicalmed9030052/s1, Table S1: Proportions of engorgement status of female Phlebotomus longipes sand flies, in urban Addis-Alem and rural Gindmeteaye.
Author Contributions
Conceptualization: W.J. and M.P.; data acquisition: W.J., E.A. and A.G.; laboratory experiments: W.J. and R.M.; analysis of the data: W.J. and M.P.; interpretation of the data: W.J., A.A., S.D., E.A., M.A., J.v.G. and A.G.; writing of the initial manuscript: W.J. and M.P.; resource coordination: M.P. and J.v.G.; manuscript revision: A.A., S.D., R.M., E.A., M.A., J.v.G. and A.G. This article includes a reflexivity statement detailing the authors’ approach to equitable international collaboration. All authors have read and agreed to the published version of the manuscript.
Funding
This work was supported by the Directorate-General development cooperation and Humanitarian Aid (DGD), under the FA4 framework collaboration of the Institute of Tropical Medicine (Antwerp, Belgium) and the University of Gondar (Gondar, Ethiopia), granted to J.v.G. and M.P. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Informed Consent Statement
All participants in whose houses sand flies were trapped were clearly informed about the study purposes and were made aware of their voluntary participation and right to withdraw at any time, without providing a reason. Verbal informed consent was obtained before trapping was performed. The study has been performed in the framework of a capacity strengthening project between the Institute of Tropical Medicine, Antwerp and the University of Gondar, Ethiopia, where the first author, W.J., is conducting his PhD under the joint supervision of A.A., S.D. and M.P. Hence, this project was a joint international collaboration between Ethiopian and Belgian partners.
Data Availability Statement
Data will be made available upon request to the authors.
Acknowledgments
The authors would like to thank the study participants in whose houses sand flies were trapped for the study. Moreover, we are grateful to the Laboratory of Microbiology, Parasitology and Hygiene at the University of Antwerp, Belgium for kindly providing laboratory-infected sand flies and thank to Leishmania research and treatment center, University of Gondar, Ethiopia.
Conflicts of Interest
The authors declare that they have no competing interests.
Abbreviations
CDC: Centers for Disease Control and Prevention; CL: cutaneous leishmaniasis; ITS-1: internal transcribed spacer 1; LRTC: Leishmaniasis Research and Treatment Center; NTD: neglected tropical disease; PCR: polymerase chain reaction; SL-RNA: spliced-leader RNA; VL: visceral leishmaniasis.
References
- Alvar, J.; Velez, I.D.; Bern, C.; Herrero, M.; Desjeux, P.; Cano, J.; Jannin, J.; den Boer, M. Leishmaniasis worldwide and global estimates of its incidence. PLoS ONE 2012, 7, e35671. [Google Scholar] [CrossRef]
- World Health Organization. Global Health Observatory Data Repository; World Health Organization: Geneva, Switzerland, 2022. [Google Scholar]
- Seid, A.; Gadisa, E.; Tsegaw, T.; Abera, A.; Teshome, A.; Mulugeta, A.; Herrero, M.; Argaw, D.; Jorge, A.; Kebede, A.; et al. Risk map for cutaneous leishmaniasis in Ethiopia based on environmental factors as revealed by geographical information systems and statistics. Geospat. Health 2014, 8, 377–387. [Google Scholar] [CrossRef] [PubMed]
- Lemma, W.; Erenso, G.; Gadisa, E.; Balkew, M.; Gebre-Michael, T.; Hailu, A. A zoonotic focus of cutaneous leishmaniasis in Addis Ababa, Ethiopia. Parasites Vectors 2009, 2, 60. [Google Scholar] [CrossRef] [PubMed]
- Bugssa, G.; Hailu, A.; Demtsu, B. The Current Status of Cutaneous Leishmaniasis and the Pattern of Lesions in Ochollo Primary School Students, Ochollo, Southwestern Ethiopia. Sci. J. Clin. Med. 2014, 3, 111–116. [Google Scholar] [CrossRef]
- Ashford, R.W.; Bray, M.A.; Hutchinson, M.P.; Bray, R.S. The epidemiology of cutaneous leishmaniasis in Ethiopia. R. Soc. Trop. Med. Hyg. 1973, 67, 568–601. [Google Scholar] [CrossRef] [PubMed]
- Bray, R.S.; Ashford, R.W.; Bray, M.A. The parasite causing cutaneous leishmaniasis in Ethiopia. Trans. R. Soc. Trop. Med. Hyg. 1973, 67, 345–348. [Google Scholar] [CrossRef] [PubMed]
- Bsrat, A.; Berhe, N.; Balkew, M.; Yohannes, M.; Teklu, T.; Gadisa, E. Epidemiological study of cutaneous leishmaniasis in Saesie Tsaeda-emba district, eastern Tigray, northern Ethiopia. Parasites Vectors 2015, 8, 149. [Google Scholar] [CrossRef]
- Amare, G.; Mekonnen, G.; Kassa, M.; Addisu, A.; Kendie, D.; Tegegne, B.; Abera, A.; Tadesse, D.; Getahun, S.; Wondmagegn, Y.; et al. First report of cutaneous leishmaniasis caused by Leishmania donovani in Ethiopia. Parasites Vectors 2023, 16, 457. [Google Scholar] [CrossRef]
- Ashford, W. Leishmaniasis Reservoirs and Their Significance in Control. Clin. Dermatol. 1996, 14, 523–532. [Google Scholar] [CrossRef]
- Mutinga, M.J.; Odhiambo, T.R. Cutaneous leishmaniasis in kenya—2. Studies on vector potential of phlebotomus-pedifer (diptera, phlebotomidae) in kenya. Insect Sci. Appl. 1986, 7, 171–174. [Google Scholar] [CrossRef]
- Svobodová, M.; Volf, P.; Votýpka, J. Experimental transmission of Leishmania tropica to hyraxes (Procavia capensis) by the bite of Phlebotomus arabicus. Microbes Infect. 2006, 8, 1691–1694. [Google Scholar] [CrossRef] [PubMed]
- Pareyn, M.; Van Den Bosch, E.; Girma, N.; Van Houtte, N.; Van Dongen, S.; Van Der Auwera, G.; Massebo, F.; Shibru, S.; Leirs, H. Ecology and seasonality of sandflies and potential reservoirs of cutaneous leishmaniasis in Ochollo, a hotspot in southern Ethiopia. PLoS Negl. Trop. Dis. 2019, 13, e0007667. [Google Scholar] [CrossRef] [PubMed]
- Pareyn, M.; Kochora, A.; Van Rooy, L.; Eligo, N.; Vanden Broecke, B.; Girma, N.; Merdekios, B.; Wegayehu, T.; Maes, L.; Caljon, G.; et al. Feeding behavior and activity of Phlebotomus pedifer and potential reservoir hosts of Leishmania aethiopica in southwestern Ethiopia. PLoS Negl. Trop. Dis. 2020, 14, e0007947. [Google Scholar] [CrossRef] [PubMed]
- Van Breugel, P.; Lillesø, J.-P.B.; Kindt, R.; Bingham, M.; Demissew, S.; Dudley, C.; Friis, I.; Gachathi, F.; Kalema, J.; Mbago, F.; et al. Potential Natural Vegetation of Eastern Africa (Ethiopia, Kenya, Malawi, Rwanda, Tanzania, Uganda and Zambia); Forest & Landscape Denmark University of Copenhagen: Hørsholm, Denmark, 2011. [Google Scholar]
- Shaira, H.; Naik, P.R.; Pracheth, R.; Nirgude, A.S.; Nandy, S.; Hiba, M.M.; Karthika, S. Epidemiological profile and mapping geographical distribution of road traffic accidents reported to a tertiary care hospital, Mangaluru using quantum geographic information system (QGIS). J. Fam. Med. Prim. Care 2020, 9, 3652. [Google Scholar]
- Lewis, D. A taxonomic review of the genus Phlebotomus (Diptera: Psychodidae). Bull. Br. Mus. 1982, 45, 121–209. [Google Scholar]
- Lewis, D.J.; Minter, D.M.; Ashford, R.W. The subgenus Larroussius of Phlebotomus (Diptera, Psychodidae) in the Ethiopian region. Bull. Entomol. Res. 1974, 64, 435–442. [Google Scholar] [CrossRef]
- Killick-Kendrick, R.; Tang, Y.; Killick-Kendrick, M.; Johnson, R.N.; Ngumbi, P.; Sang, D.; Lawyer, P. Phlebotomine sandflies of Kenya (Diptera: Psychodidae). III. The identification and distribution of species of the subgenus Larroussius. Ann. Trop. Med. Parasitol. 1994, 88, 183–196. [Google Scholar] [CrossRef]
- Abonnenc, E.; Minter, D.M. Keys for the identification of the sandflies of the Ethiopian region. Cah ORSTOM Entomol. Med. 1965, 5, 25–63. [Google Scholar]
- Kirk, K.; Lewis, D.J. Taxonomy of the Ethiopian sandflies (Phlebotomus)—II. Keys for the identification of the Ethiopian species. Ann. Trop. Med. Parasitol. 1946, 40, 117–129. [Google Scholar] [CrossRef]
- Eberhardt, E.; Van Den Kerkhof, M.; Bulté, D.; Mabille, D.; Van Bockstal, L.; Monnerat, S.; Alves, F.; Mbui, J.; Delputte, P.; Cos, P.; et al. Evaluation of a pan-Leishmania Spliced-Leader RNA detection method in human blood and experimentally infected syrian golden hamsters. J. Mol. Diagn. 2018, 20, 253–263. [Google Scholar] [CrossRef]
- Talmi-Frank, D.; Nasereddin, A.; Schnur, L.F.; Schönian, G.; Töz, S.Ö.; Jaffe, C.L.; Baneth, G. Detection and identification of old world leishmania by high resolution melt analysis. PLoS Negl. Trop. Dis. 2010, 4, 4–8. [Google Scholar] [CrossRef] [PubMed]
- R Core Team. A Language and Environment for Statistical Computing; R Core Team: Vienna, Austria, 2015. [Google Scholar]
- Yared, S.; Gebresilassie, A.; Akililu, E.; Deribe, K.; Balkew, M.; Warburg, A.; Hailu, A.; Gebre-michael, T. Diversity and altitudinal distribution of phlebotomine sand fl ies (Diptera: Psychodidae) in visceral leishmaniasis endemic areas of northwest Ethiopia. Acta Trop. 2017, 176, 1–10. [Google Scholar] [CrossRef] [PubMed]
- Calderon-Anyosa, R.; Galvez-Petzoldt, C.; Garcia, P.J.; Carcamo, C.P. Housing characteristics and leishmaniasis: A systematic review. Am. J. Trop. Med. Hyg. 2018, 99, 1547–1554. [Google Scholar] [CrossRef] [PubMed]
- Getawen, S.K.; Ashine, T.; Massebo, F.; Woldeyes, D.; Lindtjørn, B. Exploring the impact of house screening intervention on entomological indices and incidence of malaria in Arba Minch town, southwest Ethiopia: A randomized control trial. Acta Trop. 2018, 181, 84–94. [Google Scholar] [CrossRef] [PubMed]
- Votýpka, J.; Pavlasova, M.; Volfova, V.; Volf, P. Rotation of male genitalia in various species of phlebotomine sandfly. Med. Vet. Entomol. 2015, 29, 355–360. [Google Scholar] [CrossRef] [PubMed]
- Ashford, R. A possible reservoir for Leishmania tropica in Ethiopia. Trans. R. Soc. Trop. Med. Hyg. 1969, 64, 936–937. [Google Scholar] [CrossRef] [PubMed]
- Alebie, G.; Worku, A.; Yohannes, S.; Urga, B.; Hailu, A.; Tadesse, D. Epidemiology of visceral leishmaniasis in Shebelle Zone of Somali Region, eastern Ethiopia. Parasites Vectors 2019, 12, 209. [Google Scholar] [CrossRef] [PubMed]
- Ashford, R. Sandflies (Diptera: Phlebotomidae) from Ethiopia: Taxinomic and Biological Notes. J. Med. Entomol. 1974, 11, 605–616. [Google Scholar] [CrossRef]
- Aklilu, E.; Gebresilassie, A.; Yared, S.; Kindu, M.; Tekie, H.; Balkew, M.; Warburg, A.; Hailu, A.; Gebre-Michael, T. Studies on sand fly fauna and ecological analysis of Phlebotomus orientalis in the highland and lowland foci of kala-azar in northwestern Ethiopia. PLoS ONE 2017, 12, e0175308. [Google Scholar] [CrossRef]
- Gebre-Michael, T.; Balkew, M.; Gudeta, N.; Reta, M. Preliminary entomological observations in a highland area of Amhara region, northern Ethiopia, with epidemic visceral leishmaniasis. Ann. Trop. Med. Parasitol. 2007, 101, 367–370. [Google Scholar] [CrossRef]
- Odiwuor, S.; De Docker, S.; Maes, I.; Dujardin, J.; Van der Auwera, G. Natural Leishmania donovani/Leishmania aethiopica hybrids identified from Ethiopia. Infect. Genet. Evol. 2011, 11, 2113–2118. [Google Scholar] [CrossRef]
- Hadermann, A.; Heeren, S.; Maes, I.; Dujardin, J.; Domagalska, M.A.; Van Den Broeck, F.; Mauricio, I. Genome diversity of Leishmania aethiopica. Front. Cell. Infect. Microbiol. 2023, 13, 406. [Google Scholar] [CrossRef]
Figure 1.
Map of study sites [15,16]: (a) Ethiopia, with, in the northwestern Amhara region the two study districts. (b) Upper district is Lay-Armachiho, where our rural study village Gindmeteaye is situated at around 2400 m, and the lower district is Gondar Zuria, where our urban study village Addis-Alem is located at about 2100 m. (c) Zoom-in of sampling points in rural Gindmeteaye. (d) Zoom-in of sampling points in urban Addis-Alem. PD: peridomestic, IN: indoor and CA: cave collections.
Figure 1.
Map of study sites [15,16]: (a) Ethiopia, with, in the northwestern Amhara region the two study districts. (b) Upper district is Lay-Armachiho, where our rural study village Gindmeteaye is situated at around 2400 m, and the lower district is Gondar Zuria, where our urban study village Addis-Alem is located at about 2100 m. (c) Zoom-in of sampling points in rural Gindmeteaye. (d) Zoom-in of sampling points in urban Addis-Alem. PD: peridomestic, IN: indoor and CA: cave collections.
Figure 2.
Sandfly collection from three different habitats: (A) caves, (B) peridomestic (outdoor) and (C) indoor. Pictures: Wondmeneh Jemberie.
Figure 2.
Sandfly collection from three different habitats: (A) caves, (B) peridomestic (outdoor) and (C) indoor. Pictures: Wondmeneh Jemberie.
Table 1.
Species distribution of sand flies in urban Addis-Alem and rural Gindmeteaye. Proportions were calculated with the total number of sand flies of a certain sex at a certain site as the denominator (last row).
Table 1.
Species distribution of sand flies in urban Addis-Alem and rural Gindmeteaye. Proportions were calculated with the total number of sand flies of a certain sex at a certain site as the denominator (last row).
| Gindmeteaye | Addis-Alem | Overall | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| Rural | Urban | |||||||||
| Female | Male | Total | Female | Male | Total | Female | Male | Total | ||
| N (%) | N (%) | N (%) | N (%) | N (%) | N (%) | N (%) | N (%) | N (%) | ||
| Phlebotomus | ||||||||||
| P. longipes | 203 | 266 | 466 | 227 | 203 | 429 | 430 | 469 | 899 | |
| (80.2) | (89.0) | (84.9) | (69.8) | (71.0) | (70.1) | (74.7) | (80.2) | (76.6) | ||
| P. orientalis | 2 | 4 | 6 | 0 | 0 | 0 | 2 | 4 | 6 | |
| (0.8) | (1.3) | (1.1) | (0.0) | (0.0) | (0.0) | (0.3) | (0.7) | (0.5) | ||
| Sergentomyia | ||||||||||
| S. adleri | 7 | 9 | 16 | 1 | 9 | 10 | 5 | 18 | 23 | |
| (2.8) | (3.0) | (2.9) | (0.3) | (3.1) | (1.6) | (0.9) | (3.1) | (2.0) | ||
| S. clydie | 17 | 17 | 34 | 7 | 34 | 41 | 24 | 51 | 77 | |
| (6.7) | (5.7) | (6.2) | (2.2) | (11.9) | (6.7) | (4.2) | (8.8) | (6.6) | ||
| S. schwezi | 24 | 3 | 27 | 90 | 40 | 132 | 113 | 43 | 156 | |
| (9.5) | (1.0) | (4.9) | (27.7) | (14.0) | (21.6) | (19.6) | (7.4) | (13.4) | ||
| Overall total | 253 | 299 | 549 | 325 | 286 | 612 | 576 | 585 | 1161 | |
Table 2.
Seasonal distribution of female Phlebotomus longipes sand flies in urban Addis-Alem and rural Gindmeteaye in indoor and outdoor habitats. Percentages not in bold are the proportion of the sand flies within a particular habitat in a certain season, with the total number of sand flies in that season as the denominator. The percentages in bold are the proportions of sand flies captured in that certain season, with the total number of sand flies captured in that season as the denominator.
Table 2.
Seasonal distribution of female Phlebotomus longipes sand flies in urban Addis-Alem and rural Gindmeteaye in indoor and outdoor habitats. Percentages not in bold are the proportion of the sand flies within a particular habitat in a certain season, with the total number of sand flies in that season as the denominator. The percentages in bold are the proportions of sand flies captured in that certain season, with the total number of sand flies captured in that season as the denominator.
| Dry | Wet | Both Seasons | ||
|---|---|---|---|---|
| Addis-Alem (urban) | ||||
| Indoor | 49 (28%) | 30 (60%) | 79 (35%) | |
| Peridomestic | 61 (34%) | 13 (26%) | 74 (32%) | |
| Rocky/cave | 68 (38%) | 7 (14%) | 75 (33%) | |
| Total | 178 (78%) | 50 (22%) | 228 | |
| Gindmeteaye (rural) | ||||
| Indoor | 24 (31%) | 79 (63%) | 103 (51%) | |
| Peridomestic | 27 (36%) | 37 (29%) | 64 (32%) | |
| Rocky/cave | 25 (33%) | 10 (8%) | 35 (17%) | |
| Total | 76 (38%) | 126 (62%) | 202 | |
| Villages combined | ||||
| Indoor | 73 (29%) | 109 (62%) | 182 (42%) | |
| Peridomestic | 88 (34%) | 50 (28%) | 138 (32%) | |
| Rocky/cave | 93 (37%) | 17 (10%) | 110 (26%) | |
| Total | 254 (59%) | 176 (41%) | 430 | |
Table 3.
Spatio-temporal blood feeding status of female Phlebotomus longipes.
| Dry | Wet | Both Seasons | ||
|---|---|---|---|---|
| Indoor | ||||
| Blood-fed | 15 (20%) | 29 (27%) | 44 (24%) | |
| Gravid | 5 (7%) | 24 (22%) | 29 (16%) | |
| Non-fed/sugar-fed | 53 (73%) | 56 (51%) | 109 (60%) | |
| Total | 73 | 109 | 182 | |
| Peridomestic | ||||
| Blood-fed | 6 (7%) | 20 (40%) | 26 (19%) | |
| Gravid | 8 (9%) | 10 (20%) | 18 (13%) | |
| Non-fed/sugar-fed | 74 (84%) | 20 (40%) | 94 (68%) | |
| Total | 88 | 50 | 138 | |
| Caves/rocky areas | ||||
| Blood-fed | 12 (13%) | 6 (35%) | 18 (16%) | |
| Gravid | 8 (9%) | 4 (24%) | 12 (11%) | |
| Non-fed/sugar-fed | 73 (78%) | 7 (41%) | 80 (73%) | |
| Total | 93 | 17 | 110 | |
| All habitats combined | ||||
| Blood-fed | 33 (13%) | 55 (31%) | 88 (20%) | |
| Gravid | 21 (8%) | 38 (22%) | 59 (14%) | |
| Non-fed/sugar-fed | 200 (79%) | 83 (47%) | 283 (66%) | |
| Total | 254 | 176 | 430 | |
Table 4.
Spatio-temporal infection status of female Phlebotomus longipes.
| Total | Infected | ||
|---|---|---|---|
| Trap site | |||
| Addis Alem (urban) | 228 | 14 (6%) | |
| Gindmeteaye (rural) | 202 | 4 (2%) | |
| Habitat | |||
| Caves | 110 | 8 (7%) | |
| Peridomestic | 138 | 5 (4%) | |
| Indoors | 182 | 5 (3%) | |
| Season | |||
| Dry | 254 | 15 (6%) | |
| Wet | 176 | 3 (2%) | |
| Blood feeding status | |||
| Non-fed | 283 | 10 (4%) | |
| Blood-fed | 88 | 5 (6%) | |
| Gravid | 59 | 3 (5%) | |
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content. |
© 2024 by the authors. Licensee MDPI, Basel, Switzerland. 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/).
Share and Cite
MDPI and ACS Style
Jemberie, W.; Animut, A.; Dugassa, S.; Gebresilassie, A.; Melkamu, R.; Aklilu, E.; Aemero, M.; van Griensven, J.; Pareyn, M. Ecology and Infection Status of Sand Flies in Rural and Urban Cutaneous Leishmaniasis Endemic Areas in Northwest Ethiopia. Trop. Med. Infect. Dis. 2024, 9, 52. https://doi.org/10.3390/tropicalmed9030052
AMA Style
Jemberie W, Animut A, Dugassa S, Gebresilassie A, Melkamu R, Aklilu E, Aemero M, van Griensven J, Pareyn M. Ecology and Infection Status of Sand Flies in Rural and Urban Cutaneous Leishmaniasis Endemic Areas in Northwest Ethiopia. Tropical Medicine and Infectious Disease. 2024; 9(3):52. https://doi.org/10.3390/tropicalmed9030052
Chicago/Turabian StyleJemberie, Wondmeneh, Abebe Animut, Sisay Dugassa, Araya Gebresilassie, Roma Melkamu, Esayas Aklilu, Mulugeta Aemero, Johan van Griensven, and Myrthe Pareyn. 2024. "Ecology and Infection Status of Sand Flies in Rural and Urban Cutaneous Leishmaniasis Endemic Areas in Northwest Ethiopia" Tropical Medicine and Infectious Disease 9, no. 3: 52. https://doi.org/10.3390/tropicalmed9030052
APA StyleJemberie, W., Animut, A., Dugassa, S., Gebresilassie, A., Melkamu, R., Aklilu, E., Aemero, M., van Griensven, J., & Pareyn, M. (2024). Ecology and Infection Status of Sand Flies in Rural and Urban Cutaneous Leishmaniasis Endemic Areas in Northwest Ethiopia. Tropical Medicine and Infectious Disease, 9(3), 52. https://doi.org/10.3390/tropicalmed9030052
