- Open Access
Bovine fasciolosis at increasing altitudes: Parasitological and malacological sampling on the slopes of Mount Elgon, Uganda
© Howell et al.; licensee BioMed Central Ltd. 2012
- Received: 14 April 2012
- Accepted: 14 August 2012
- Published: 7 September 2012
To clarify the extent and putative transmission zone of bovine fasciolosis on the slopes of Mount Elgon, Uganda, conjoint parasitological and malacological surveys, inclusive of inspection of animals at slaughter, were undertaken at increasing altitudes.
A total of 239 cattle were sampled across eight locations ranging in elevation from 1112-2072 m. Faecal material was examined for presence of Fasciola eggs and sera were tested by ELISA for antibodies against Fasciola antigens. Bolstering this, 38 cattle at slaughter from 2 abattoir sites at 1150 m and 1947 m were inspected; in addition, wild buffalo stool (n = 10) opportunistically picked within Mount Elgon National Park (MENP) at 3640 m was examined. By faecal egg detection, prevalence of Fasciola gigantica at low (<1500 m) and high (>1500 m) altitude sites was 43.7% (95% CI 35.4-52.2) and 1.1% (95% CI 0.0-6.0), respectively, while by ELISA was much higher, low altitude - 77.9% (95% CI 69.7-85.4) and high altitude - 64.5% (95% CI 51.3-76.3). The decline in prevalence with increasing altitude was corroborated by abattoir sampling. Thirty seven aquatic habitats, ranging from 1139-3937 m in altitude were inspected for freshwater snails, 12 of which were within MENP. At lower altitudes, Lymnaea (Radix) natalensis was common, and often abundant, but at higher altitudes became much rarer ceasing to be found above 1800 m. On the other hand, Lymnaea (Galba) truncatula was found only at altitudes above 3000 m and within MENP alone. The snail identifications were confirmed by DNA analysis of the ribosomal 18S gene.
Active infections of F. gigantica in cattle are common in lower altitude settings but appear to diminish with increasing elevation. This is likely due to a growing paucity of intermediate hosts, specifically populations of L. natalensis for which a natural boundary of 1800 m appeared. Although F. hepatica was not encountered, the presence of several populations of L. truncatula at elevations over 3000 m point towards a potential transmission zone within MENP should this parasite be introduced.
- Body Condition Score
- Liver Fluke
- Freshwater Snail
- Transmission Zone
- High Altitude Site
Fasciolosis, caused by infection with the liver fluke Fasciola, can cause significant economic losses in African livestock [1, 2]. The complex nature of the lifecycle and epidemiology of this snail-borne disease presents challenges for predictive mapping at the herd-level, as well as disease management and animal husbandry at the individual-level . Fasciola gigantica and Fasciola hepatica can infect a wide variety of domesticated animals, wildlife and people [4–9]. Thus the disease-endemic zone can be difficult to define from parasitological data alone and so consideration of the distribution of associated snail intermediate hosts can be important . F. gigantica is the most common liver fluke in sub-Saharan Africa, being adapted to warmer conditions  likely due to the widespread distribution of its intermediate host Lymnaea (Radix) natalensis . On the other hand owing to a more limited distribution of its intermediate host Lymnaea (Galba) truncatula , F. hepatica can exist in zoonotic foci which are more restricted to cooler regions of Africa, including Kenya, Ethiopia and Tanzania [1, 10, 13]. Nonetheless, actual or potential overlap of both types of fasciolosis can occur especially where snail-habitats converge, for example, with increasing altitude as in the highlands of Ethiopia  or perhaps in upland zones of eastern Uganda, as yet to be fully explored. In the Mount Elgon area of Uganda, fasciolosis is poorly studied as there is no systematic veterinary or medical disease surveillance system.
Cattle are Uganda’s most economically important livestock species with an estimated population of 11 million . The majority are either indigenous Zebu or Sanga, with less than 5% being imported ‘exotic’ breeds, mainly Friesians . Livestock production is hampered by many disease constraints of which fasciolosis is considered the most important helminth infection . The Mount Elgon region consists of predominately rural subsistence farmers covering a zone between 1000-2300 m in altitude rising towards an important wildlife reserve, the Mount Elgon National Park (MENP). Encompassing a total area of some 1,145 km2, MENP commences at 2300 m and extends to 4321 m at Wagagi Peak. Within the park, a number of herds of wild ruminants are known including buffalo, antelope and elephant but illegal cattle trading routes, from Uganda to Kenya and vice versa, traverse throughout. However, with increasing Uganda Wildlife Authority (UWA) foot patrols servicing an increasing hiking and camping tourism, illegal cattle trafficking has declined in recent years.
Like elsewhere in Uganda, the lowland areas of Mount Elgon are known to be endemic zones for F. gigantica with reports documenting the prevalence of F. gigantica at 54.7% in cattle [16, 18, 19]. A contemporary situational analysis, however, is yet lacking. From a malacological perspective, there has been no update to the formal snail surveys conducted by Georg Mandahl-Barth and by Hubendick in their general treatise on Ugandan freshwater snails and Lymnaea, respectively over 50 years ago [12, 20]. Both Lymnaea natalensis and Lymnaea mweruensis have been reported from the area with the latter species now considered synonymous with Lymnaea truncatula, as collected by C.C. Cridland from Sasa River Camp at 2900 m (now within MENP). Such upland areas, like those in neighbouring Tanzania, are thought suitable zones for the transmission of F. hepatica, for example, L. truncatula being recently found at 2712 m & 2720 m with identifications confirmed by DNA analysis of the ribosomal 18S . Though F. hepatica has yet to be encountered in natural transmission cycles in Uganda, it has been known from earlier reports within UK-imported cattle .
Clearly defining such local zones of transmission in eastern Uganda is also important for further modelling of the suitability of habitats elsewhere in East Africa. Various authors have designed models based on climate and intermediate host presence to predict the prevalence of Fasciola spp. [14, 22]. However, areas that appear broadly similar in terms of climate can have very different snail populations due to variations in micro-climate and local aquatic factors, e.g. water pH and conductivity. This limits the accuracy of such climatic models, and localised parasitological and malacological data are still required for prediction of actual disease zones or outbreaks [22, 23]. In many countries, signalment of cattle condition  and subsequent meat inspection provides an opportunity to monitor the incidence of fasciolosis, also allowing access to adult worms enabling morphological identification [23, 25]. However, it is not able to detect past infections in those animals that have either been treated or developed immunity and self-cured. A suitable immunological test could fill this gap, and also detect pre-patent infections, but presently this is only available for assaying antibody titres in cattle to excretory/secretory (ES) antigens of F. hepatica . With this assay, heterologous reactions to F. gigantica are likely but as yet not known, however, serological testing should be an interesting adjunct in revealing putative transmission zones.
Using a combination of parasitological sampling, bolstered by experimental serology, our study aimed to investigate the occurrence of fasciolosis in bovids at low and high altitude areas on the slopes of Mount Elgon and also assessed animal condition (i.e. body signalment). The parasitological surveys were complemented with a conjoint malacological appraisal in an attempt to better define the actual or potential disease transmission zone of these parasites.
Study area and design
At each of the six main sites, at least 30 cattle were sampled, a maximum of two per owner in order to avoid bias due to multiple animals from the same herd having similar risk factors. Where possible, stool and blood specimens were taken from each animal at the time of tethering. At four of these sites, convenience sampling was employed, with local community leaders mobilising farmers to bring their animals to a central point. At two of the sites this method was unsuccessful and individual households around a central point were visited. From the two large roving herds in between Kapchorwa and Ngenge, a random selection of 10 cattle from each were sampled. Additionally, during a three-day trek on foot to altitudes of between 3000-4000 m in MENP, freshly deposited buffalo stool samples (n = 10) were opportunistically picked from the ground at an elevation of 3900 m at a unique grazing site adjacent to a hot spring.
Signalment of cattle
The data on signalment of each cow were recorded as follows: Age category - calf (approximately 2 weeks to 6 months), sub-adult (6 months to 18 months), or adult (18 months plus); sex; breed - Friesian, local (zebu type) or hybrid; and body condition score (BCS) graded through 1 to 5 classifications according to Roche .
Faecal egg detection
Faecal samples were obtained per rectum or taken from the ground if seen to have been directly produced. Approximately 3 g of stool was thoroughly mixed into 250 ml of bottled mineral water containing 0.5% Tween-20 (Sigma-Aldrich, UK) before filtration-concentration; two methods were each used for the isolation of eggs from faeces. ‘Individual stool’ was analysed using Flukefinder® kit (see http://www.flukefinder.com) and in an attempt to confirm these individual findings ‘pooled stool of 10 animals’ was subjected to standard coprological filtration with a descending pore series of 3 large-diameter metal sieves (at 425, 125, and 32 microns respectively) following . Faecal eggs, from liver flukes or paramphistomes, were finally collected in a 10 cm glass petri-dish stained with a few drops of 10% methylene blue solution, viewed and counted under the dissecting microscope at x40 magnification .
Blood sampling and serology
Blood was obtained from an ear vein and harvested into sterile 10 ml plastic syringes and allowed to clot in a 1.5 ml eppendorf tube. Serum was then separated by centrifugation, and heat-inactivated by incubation at 56°C for 30 min, as required for importation licensing by the Department for the Environment, Food and Rural Affairs (DEFRA), UK. After heat-inactivation samples were stored in liquid nitrogen before transportation to the UK. ELISA was performed according to [26, 29] with the following minor modifications: The concentration of F. hepatica E/S antigens used to coat the ELISA plate was 1 mg/ml; the concentration of monoclonal anti-bovine IgG used was 1:70,000 (this was first optimised by a checkerboard titration); and 20 minutes following the addition of TMB substrate, 100 μl of stopping solution (0.5 M HCL) was added to each well prior to reading. The results are given as the mean of the optical density (OD) obtained from duplicate samples expressed as a percentage of the strong positive control (PP), with PP of 15 or above considered a positive result [26, 29].
Livers obtained from cattle slaughtered at Mbale (n = 30) and Kapchorwa (n = 8) abattoirs, at 1150 m and 1947 m, were inspected for flukes by cutting open the main bile ducts into the liver parenchyma. Adult flukes were identified morphologically based on size and shape [30, 31]. Faecal and blood samples were taken from the large intestine and mesenteric vein respectively and processed as described above for ELISA.
In total 37 freshwater sites, ranging in altitude from 1139 m to 3937 m above sea level, were selected and surveyed for aquatic snails. Sites were chosen to include a variety of streams, marshes and pools to cover as wide an area as possible, within easy reach of vehicular access, with the exception of the sites above 3000 m within MENP that were visited on foot. Using collecting sieves and snail scoops, two people surveyed each site for 10 minutes and all collected snails were counted. If there were different types of habitat within each location, for example, slow/fast flowing water within streams or drainage ditches, these were all surveyed. The presence and numbers of each species of snail were recorded according to field identification keys of Brown . To later confirm the identification of encountered lymnaeids, a selection of snails was placed in 70% ethanol for DNA analysis. Spot-site water chemistry readings were taken for pH, conductivity, total dissolved salt and temperature from each of the different habitats using a handheld water meter (Hanna H1-9816-6; VWR, UK) to investigate ecological associations.
DNA-based snail identification
Genomic DNA was extracted from a total of 16 snails representative of L. natalensis (n = 8) and L. truncatula (n = 8) using the DNeasy Blood and Tissue Kit (QIAGEN, Germany). A 450 base pair region of the nuclear ribosomal 18S was amplified by PCR with the primers 18SLYMFOR 5′ agtagtcatatgcttgtctcaaagattaagcca and 18SLYMREV, 5′ tgcgcgcctctgccttccttggatgtggtagccgt, following Stothard . Amplification products were purified using the QIAquick PCR Purification Kit (QIAGEN, Germany) and sequenced using the ABI PRISM™ BigDye Terminator Cycle Sequencing Ready Reaction Kit (Applied Biosystems, UK). Sequencing chromatograms were produced by the DNA Sequencing Facility, The Natural History Museum, London, UK and analyzed using DNASTAR’s Lasergene Sequence Analysis Software (Madison, USA). Compiled sequences were aligned and also compared with other lymnaeids on GenBank. The putative secondary structure of the variable V2 E10-1 helix was investigated using the RNAfold web server (http://rna.tbi.univie.ac.at/) and compared to that described by Stothard and Bargues & Mas-Coma [33, 34]. To investigate known restriction site variation, amplification products were also digested, separately, with either msp I or cfo I enzymes and subsequently separated by PAGE and ethidium bromide staining according to , and photographed with a Gel Doc E2 Imager (BioRad, UK).
For raw prevalence data, exact binomial confidence intervals were calculated for the cattle surveys using Stata v. 9 (2007, Texas, 77845). Other tests were performed using PASW v. 18 (2010, SPSS Inc, Chicago). Poisson regression was used for multivariate association with snail data and recorded environmental variables. Firstly, parameters with close correlations (>0.8) were excluded from being modelled together. Secondly, each parameter was entered separately and the model with the smallest difference between scaled deviance and degrees of freedom taken as being the most representative.
Biometric data assessing signalment of cattle sampled for fluke infection at high (n = 145) and low (n = 94) altitudes [95% confidence intervals are shown]
Low altitude < 1500 m
High altitude > 1500 m
Percentage (95 % CI)
Body condition score
Underweight (BCS 1-2)
Faecal egg count analysis
Prevalence of Fasciola infections as detected by faecal egg detection, ELISA and gross liver inspection at abattoir [95% confidence intervals are shown in brackets]
Low altitude < 1500 m
High altitude > 1500 m
Owing to resource constraints and sampling spoiling, a sub-set of animals were tested by ELISA, finding that 64.5% (95% CI = 51.3-76.3) of cattle at high altitude were positive for Fasciola spp. whereas 77.9% (95% CI = 69.7-85.4) of cattle at low altitude were positive, Table 2. This was a statistically significant difference, however, as the high ELISA positive rate was not confirmed by egg detection in the high altitude samples (i.e. confirmation of active infections), only egg detection results are used for subsequent analysis and further discussion.
Livers from 30 animals originating at low altitude and 8 from high altitude were inspected. The proportion of animals infected with liver fluke at the low altitude sites was 48.4% (95% CI 30.2-66.9). At the high altitude sites, none (95% CI 0.0-37.9) of the animals were found to be infected, Table 2. Owing to time constraints within slaughter houses, numbers of flukes found were not recorded, but in the majority of animals less than 10 flukes were found. Based on body size and shape, all flukes found were confidently identified as F. gigantica, there was no evidence of F. hepatica-like worms.
Lymnaea natalensis was found at 12 sites ranging in altitude from 1139 m to 1770 m. By contrast L. truncatula was found at only 5 sites, all above 3500 m. There was no geographical overlap between the two species, with the zone between 1800 m and 3500 m being a lymnaeid-free zone, Figure 1.
Results of Poisson regression on collected snail and aquatic habitat data
Included in model
Elevation (100 m)
Concentration (10 ppm)
Elevation (100 m)
Conductivity (10 μs)
Location and occurrence of snails at each of the 37 collection sites
GPS location (in decimal seconds)
Lymnaea spp. (n)
Other genera present
L. natalensis (2)
L. natalensis (36)
L. natalensis (2)
L. natalensis (2)
L. natalensis (9)
L. natalensis (2)
L. natalensis (12)
L. natalensis (3)
L. natalensis (45)
L. natalensis (25)
L. natalensis (7)
L. natalensis (6)
L. truncatula (4)
L. truncatula (12)
L. truncatula (24)
L. truncatula (49)
L. truncatula (30)
DNA-based snail identification
Taken together the parasitological and malacological surveys have shown that fasciolosis, resultant from F. gigantica, was widespread in cattle at lower altitudes in the Mount Elgon area, however, defining where the actual transmission zone ends is, however, problematic; especially so given the existence of suitable intermediate snail hosts up to 1800 m. Moreover, the confirmation of several populations of L. truncatula within the MENP, a single population being reported over 50 years ago , raises some potential concerns for transmission of F. hepatica should this parasite ever be introduced into this area.
Observations associated with increasing altitude
Within the cattle sampled at altitudes between 1000 m and 1500 m, F. gigantica was shown to be present by all diagnostic methods used. The egg-patent prevalence by Flukefinder® was 44%, Table 2. This is in agreement with the earlier findings , however, between the altitudes of 1500 m and 3000 m only a single Fasciola egg positive cow was identified so it can be firmly considered that F. gigantica worms were not present in significant numbers, despite inferences from ELISA which is semi-quantitative for F. hepatica, at these elevations. This decline is concurrent with the growing scarcity of local L. natalensis populations, ceasing at 1800 m. Perhaps the presence of such snail hosts is a useful environmental indicator of the potential for disease transmission which can be provided relatively quickly during field-excursions as freshwater snails with dextral shell without an operculum are readily distinctive.
A key finding in this study is the dichotomy between the presence of L. natalensis at sites below 1500 m and L. truncatula at sites above 3000 m. Inspection for snails at the Sasa River Camp within MENP did not reveal the presence of lymnaeids, unlike during the 1950s where L. truncatula (mweruensis) was encountered . The analysis of snail DNA very clearly confirmed the latter species likely of European origin [34, 35]. The precise reasons for this lower altitudinal occurrence of L. truncatula are open to conjecture but could include longer-term climatic changes in the area restricting the suitable habitat to higher elevations with general climate warming. In other studies, L. natalensis shedding Fasciola have been found at altitudes of 2667 m in Kenya . This perhaps indicates that factors other than altitude and the typically associated temperature are likely to be having an effect. There were wide variations in water temperature, water chemistry, vegetation (see Figure 4) and soil type.
Although altitude and temperature follow a fairly predictable trend across a wide area of East Africa, other factors such as snail habitat are much more variable, this study identified many sites where no snails were found, despite having similar temperatures to nearby sites where snails were plentiful. The apparent ‘random’ focalisation of snails in aquatic habitats is known likely to be due to cryptic micro-habitat associations and to the vagrancies of population colonisation . In the regression model, for example, the input factors were a poor predictor for actual snail numbers. More generally, the presence of F. gigantica at altitudes above 1500 m and the absence of F. hepatica at altitudes above 1200 m conflicts with general model-based assumptions on temperature alone [14, 22]. Micro-climates suitable for snails to survive can occur in otherwise hostile environments, but may be hard to find without more exhaustive sampling . Furthermore, the ability of snails to aestivate, differences in annual transmission patterns and the timing of surveys have significant bearings upon the findings but there were no obvious differences in presence/absence of snails recorded in the March and June-July surveys.
Within the MENP and at altitudes above 3000 m, only L. truncatula was found alongside an enigmatic Bulinus population at high altitude, (see Table 4), tentatively identified of the B. truncatus/tropicus group . Despite the presence of L. truncatula, there was no evidence of Fasciola spp. infection in the sampled buffaloes although paramphistomes were common. It could be concluded that local conditions are not suitable for the transmission of F. hepatica or perhaps that this parasite has yet to be introduced to this area. The MENP also extends into Kenya, where other livestock and people live together at higher altitudes. As F. hepatica is known to exist within natural transmission cycles in the neighbouring highlands of Kenya  this could be a potential route for the introduction of F. hepatica into the Ugandan highland region. Conversely, there was no evidence that L. truncatula was present at sites at lower altitudes where cattle were kept. Nonetheless, this snail species can be present at much lower altitudes in other countries , hence there may be some potential for this lymnaeid to establish in the 1500-2500 m zone, so further sampling should not neglect this possibility.
Implications for control and disease surveillance
From the available evidence, no community-based intervention is currently needed for management of fasciolosis in domestic cattle at altitudes above 1500 m in this Mount Elgon area. At low altitude, however, future interventions based upon de-worming are clearly worthwhile in addition to the collection of local information on farming practices, economic impact and animal trafficking. The latter is especially important with future cattle re-stocking planned from this area to central regions of Uganda (Lira/Kitgum/Gulu) following the cessation of civil insecurities. The inspected herds at Ngenge, for example, have been ear-marked for this restocking programme.
In terms of future disease surveillance the detection of populations of L. truncatula in several sites frequented by UWA patrols and hiking tourists, raises some concerns of the safety of environmentally drawn water. Although the existence of F. hepatica has yet to be proven in this area, it would be advisable to raise awareness of fluke-borne diseases in general. More broadly, we are presently PCR screening the collected snails for evidence of fluke infections in an attempt to investigate these more cryptic aspects of parasite transmission.
From parasitological sampling and observations at slaughter, infections of F. gigantica in cattle are common in lower altitude settings but appear to diminish with increasing elevation. This is most likely due to a growing paucity of L. natalensis within the environment, with a natural boundary of approximately 1800 m where no further populations of L. natalensis were found. Whilst F. hepatica was not encountered during these surveys, the presence of L. truncatula at elevations over 3000 m point towards a potential transmission zone within MENP should this parasite be introduced to this part of East Africa. Greater vigilance of this parasite within imported cattle, and possibly within local people, should therefore be encouraged.
We would like to thank the field team from Vector Control Division who assisted during the surveys and local staff within the District Veterinary Offices, also the participation of the farmers who brought their animals for inspection. We especially thank Andrew Ruggiana for his assistance in the field with really expert cattle handling.
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