Multilingual abstracts

Please see Additional file 1 for translations of the six official working languages of the United Nations.

Background

In many African countries large dams have been constructed for hydropower production, while small multipurpose dams aim at enhanced agricultural production and livestock breeding [1]. Environmental transformation deriving from the construction and operation of water resources are root causes for the emergence and intensification of infectious diseases transmitted by mosquito vectors (e.g. lymphatic filariasis and malaria) and snail intermediate hosts [2,3,4,5,6,7]. In Africa, snails of the genera Biomphalaria and Bulinus act as intermediate hosts for Schistosoma mansoni and S. haematobium, respectively [8, 9]. Snail habitats are diverse and the transmission of schistosomiasis is governed by human-water contact patterns [10, 11]. Hence, communities living in close proximity to infested water bodies are at risk of schistosomiasis [12].

In Côte d’Ivoire, Biomphalaria pfeifferi is the sole intermediate host of S. mansoni, while Bulinus truncatus and Bu. globosus are transmitting S. haematobium [13]. The construction of major water resource development projects goes back to the early 1970s. For example, two large dams were constructed on the Bandama River; i.e. Lake Kossou (completed in 1972) and Lake Taabo (filled in 1979). Both dam constructions were associated with outbreaks of S. haematobium [14]. In addition to large dams, more than 500 small multipurpose dams were built in the northern and central parts of Côte d’Ivoire [15,16,17]. The aim of this study was to deepen the understanding of the presence and dynamics of freshwater snail populations in the context of a hydro-agricultural development, placing particular emphasis on intermediate host snails of schistosomiasis. For this purpose, our study covered the phases of dam construction into the first years of intensified agricultural production. The investigation was carried out in the transition zone between savannah in the north and tropical rainforest in the south of Côte d’Ivoire. Our research aims at contributing to the prediction of the transmission of schistosomiasis and informing surveillance-response systems to prevent and control schistosomiasis in areas characterised by profound environmental transformation.

Methods

Ethics statement

This study was approved by the institutional research commission of the Centre Suisse de Recherches Scientifiques en Côte d’Ivoire (CSRS) and received approval by Bouaké’s health authorities. In each village, permission to work was granted by local chiefs. Community members were informed in detail about the objectives, procedures, and potential risks and benefits related to the study. Illiterate people were orally informed in the local language. Written informed consent was obtained at the beginning of the study from adult participants or from parents/guardians of children aged less than 18 years old. People found with Schistosoma infection were treated with praziquantel (40 mg/kg of body weight) while a single oral dose of albendazole (400 mg) was given to individuals with soil-transmitted helminth infection.

Study area and population

The study was carried out in five villages located in proximity to a small multipurpose dam (i.e. Ahougui, Koffikro, Kpokahankro, N’Douakro and Raffierkro) [18] and two villages without activities in proximity to the small dam (i.e. Mamian and N’Drikro). All villages were located near Bouaké, in the central part of Côte d’Ivoire (geographical coordinates 7°44’ N latitude and 5°41’ W longitude) as shown in Fig. 1.

Fig. 1
figure 1

Map of study site near Bouaké, central Côte d’Ivoire

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During the study period from 2007 to 2012, the daily average temperature ranged between 23.7 °C and 33.8 °C with an average annual rainfall of 1 229 mm and 1 350 mm. The local humid tropical climate zone is characterised by two well-defined seasons: a dry season from November to February and a long rainy season from March to October. The vegetation is typical for the transition zone from tropical rainforest to savannah. Before dam construction, people were mainly engaged in subsistence agriculture (e.g. cassava and yams). Construction of the dam provided new opportunities for local dwellers, including irrigated rice cultivation, vegetable farming and inland fish production.

Study design

This study was designed as a repeated cross-sectional survey implemented over a six-year period. During the construction of the multipurpose dam, from June 2007 to November 2009, nine malacological (M1–M9) and three parasitological (P1–P3) surveys were carried out capturing the main phases of project development (see Fig. 2): (i) the construction of the dam; (ii) the construction of the irrigation canals, agricultural fields and fish ponds; and (iii) the growing of rice-fields. In the early stages of the dam operation, the parasitological surveys were continued from 2010 to 2012 (P4–P6; in the months of June/July) for the follow up.

Fig. 2
figure 2

Study area near Bouaké in central Côte d'Ivoire, showing the location of the study villages within the irrigation scheme, different activities around the multipurpose dam and month of malacological and parasitological surveys

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Malacological surveys

In each study village, all the water contact sites where people used to collect water, wash clothes, bath, swim and play (young children) were surveyed. Snail sampling was undertaken by two experienced field collectors using scoops and forceps for the duration of 15 min. Snail habitats were characterised using a standard form. The collected snail specimens were transferred in perforated plastic boxes to a nearby laboratory. Snails were identified according to shell morphology and structure using standard identification keys [19, 20]. After genus and/or species identification, potential intermediate host snails were tested over a one-month period for Schistosoma cercaria shedding in their swimming water after two–three hours of exposure to sunlight during five times points: the day of collection and 1, 2, 3 and 4 weeks after collection. Subsequently cercariae shedded were morphologically identified through identification keys put forward by Frandsen and Christensen [21].

Parasitological survey

A total sample size of 600 individuals was the set target for the parasitological survey, representing 50% of the total population in the study area. For accounting for the different population numbers in the study villages, sampling proportional to size was applied. Households were randomly selected from previously prepared household list and children aged 6–15 years attending primary school were invited to participate in the survey. In addition, all primary schoolchildren from Raffierkro, N’Drikro and Mamian were screened. After informed consent, stool and urine samples were collected with the assistance of local nurses. Two plastic containers (125 ml) were distributed to each adult participant the day before the sample collection. Participants were invited to submit a sample of their own morning stool and urine in two separate collection containers. Each participant was given a unique identification number. The samples obtained were then transferred to a nearby laboratory and worked-up the same day for S. haematobium (urine), S. mansoni and soil-transmitted helminths (stool) using standardised, quality-controlled methods. In brief, stool samples were processed by the Kato-Katz technique, producing two thick smears per stool per participant [22]. After a clearing time of 30–45 min, Kato-Katz thick smears were examined under a microscope by experienced laboratory technicians. Helminth eggs were counted and recorded on a species-specific level. Individual egg output was expressed as eggs per gram of faeces (EPG), which was calculated as the arithmetic mean egg count from two readings multiplied by a factor of 24. The prevalence and intensity of S. haematobium infection were estimated based on a urine filtration method. In brief, 10 ml of urine was pressed through a polyamide (Nytrel) filter (mesh size: 20 μm) and stained with a drop of Lugol’s solution for subsequent microscopic examination. The intensity of S. haematobium infection was expressed as the number of eggs per 10 ml of urine.

Statistical analysis

Double entry of data using Excel (Microsoft; Redmond, WA, USA) was done and cross-checked with EpiInfo version 3.2 (Centers for Disease Control and Prevention; Atlanta, GA, USA). The final database was analysed using STATA version 9.0 (Stata Corporation, College Station, TX, USA). The Kruskal-Wallis (KW) test was employed to compare the differences in snail densities among villages. Pearson’s χ 2 test was used to compare proportions between villages, age categories and sex. The Student’s t-test was used to compare means. For all statistics, a P value below 0.05 was considered as statistically significant.

Results

Water contact sites and snail composition

A total of 20 human water contact sites were recorded: eight in Kpokahankro, five in Raffierkro, three in Ahougui and N’Douakro each and one in Koffikro. A total of 1 700 freshwater snails were collected from the sampling sites (Table 1). Identification based on shell morphology revealed nine genera. Snails belonging to the genera Bulinus and Pila were observed in all the localities, whereas the genera Biomphalaria, Lymnaea, Physa and Melanoides were observed in only two localities (Ahougui and Raffierkro). In the early construction phase (year 2007), 65 snails belonging to three species were collected. Bi. pfeifferi in Ahougui, Bu. forskalii in Kpokahankro and Raffiekro and P. acuta in Raffiekro. During this period the intermediate host Bi. pfeifferi was observed only in Ahougui with 13 individuals.

Table 1 Snail abundance in a study carried out near Bouaké in central Côte d'Ivoire between June 2007 and November 2009, stratified by study period and village
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In 2008 (advanced construction phase), 1 260 snails, including the three intermediate hosts Bi. pfeifferi, Bu. truncatus and Bu. globosus, were collected. Most of them (n = 1 027; 81.5%) were observed in Raffierkro. In the same village Bi. pfeifferi was the predominant species (64.3%), followed by Bu. globosus (11.3%) and Bu. truncatus (10.2%). In 2009 (late construction phase), the same species were observed, though with a decrease in the number of individuals for each of the three species.

Over the entire malacological study period (June 2007–November 2009), the highest number of intermediate host snails was recorded in Raffierkro. Bi. pfeifferi was the most frequently encountered intermediate host snail in Raffierkro (n = 725; 42.6%), followed by Bu. globosus (n = 205; 12.1%) and Bu. truncatus (n = 214; 12.6%). M. tuberculata was the predominant snail species in Ahougui (n = 136; 55.3%), while Bu. forskalii dominated in Kpokahankro (n = 117; 77.0%) and N’Douakro (n = 5; 55.3%). In Ahougui, few Bi. pfeifferi (n = 13) and Bu. truncatus (n = 3) were collected during the first and the third year of the study, respectively.

Habitats and density of schistosomiasis intermediate host snails

The key habitats where snails were observed consisted of canals, the dam, paddies, swamps and water reservoirs. The mean snail abundance varied significantly across the four villages (KW = 136.5; P = 0.025), with Raffierkro recording the highest abundance.

The density of schistosomiasis intermediate host snails was highest in Raffierkro. As shown in Fig. 3, during the second time-period, from June to November 2008, the number of Bi. pfeifferi increased rapidly from 0 to 449 snails. Subsequently, numbers decreased progressively from 211 to 46 and six snails from February to November 2009. With regard to Bu. globosus, two peaks of relative abundance were observed in November 2008 and June 2009, while Bu. truncatus showed only one peak (November 2008). No Bu. globosus snails were observed in February 2009, while Bu. truncatus population decreased. The maximum abundances of Bu. globosus (n = 89) and Bu. truncatus (n = 54) individuals were observed, in June and November 2009, respectively. Overall, density of snails collected in Ahougui was lower compared to Raffierkro.

Fig. 3
figure 3

Density of the three intermediates host snail species of schistosomiasis in Raffierkro from June 2007 to November 2009

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Infection of snails

None of the snails was found shedding schistosome cercariae. Yet, some snails were found shedding zoophilic cercariae, such as Strigeides, and Xiphidio-cercariae.

Study adherence and population characteristics

In June 2007, stool and urine samples could be obtained from 534 and 551 people, respectively. In the last survey round conducted in June 2009, 389 and 359 stool and urine samples were obtained, respectively. The study population was mainly composed of individuals above 15 years (54.8%). From June 2007 to June 2012, all primary schoolchildren from Raffierkro, N’Drikro and Mamian were screened.

Prevalence and intensity of Schistosoma infections by sex and age

The cumulative prevalence for the two Schistosoma species in the five study villages was significantly lower in 2009 (2.6%, 95% CI: 1.1–5.0%), compared to the baseline cross-sectional survey in 2007 (7.5%, 95% CI: 5.4–10.1%). This difference was statistically significant (χ 2 = 7.97; P = 0.005). In Table 2, the overall prevalence of Schistosoma infection in individual villages was below 6.0% at the time of the baseline assessment in 2007. Prevalences remained at similar levels during the two follow-up surveys, except for Raffierkro, where a higher prevalence was observed in 2007 (P = 0.005), associated with a difference in the prevalence between males (10.5%) and females (4.9%) (χ 2 = 5.88; P = 0.024). In the dam area, the global prevalence observed of S. mansoni was very low at 0.4% in 2007 and 0.3% in 2009. No infected people were observed in Ahougui, Koffikro, N’Douakro and Kpokahankro. In Raffierkro, the prevalence decreased from 1.3% to 0.7% from 2007 to 2009, respectively. All cases detected were restricted to school-aged children (6–15 years) (Table 3). The intensity of infection was very low in both 2007 and 2009 (0.01 EPG, 95% CI: 0–0.03 EPG).

Table 2 Prevalence of S. haematobium and S. mansoni in the study villages near Bouaké in central Côte d'Ivoire in proximity to dam between June 2007 and November 2009
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Table 3 Prevalence of S. haematobium in the five study villages near Bouaké in central Côte d'Ivoire, stratified by age category between 2007 and 2009
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The prevalence of S. haematobium was also low, decreasing from 6.9% (95% CI: 4.7–9.0%) in 2007 to 2.2% (95% CI: 0.7–3.8%) in 2009 (χ 2 = 9.86; P = 0.002). Although the prevalence was low, a significant sex difference was observed. In 2007, males showed a significantly higher prevalence than female (9.6% versus 4.7%; χ 2 = 5.20; P = 0.022). In 2009, the prevalence remained comparable (χ 2 = 0.38; P = 0.54), except for Raffierkro, where a prevalence of 15.4 and 3.1% was recorded in 2007 and 2009, respectively

The geometric mean of excreted eggs/10 ml of urine was low throughout, with an observed decrease from 0.15 eggs/10 ml (95% CI: 0.09–0.21 eggs/10 ml) in 2007 to 0.05 eggs/10 ml (95% CI: 0.01–0.10 eggs/ml) in 2009 (P = 0.70).

Considering schoolchildren in 2007, a difference was observed in the prevalence of S. haematobium between Raffierkro and the two schools of Mamian and N’Drikro. The prevalence of infection in Raffierkro’s school decreased from 13.9% (95% CI: 8.3–19.4%) to 2.9% (95% CI: 0.4–6.2%) in 2009. During the 2010 and 2011 cross-sectional surveys, no Schistosoma infection was observed in the three schools. In 2012, only one and four cases were observed in Raffierkro and N’Drikro, respectively (Table 4). All of these cases were detected in children aged between six and ten years.

Table 4 Prevalence of schistosomiasis in children 6–15 years in the five study villages near Bouaké in central Côte d'Ivoire from 2007 to 2012
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Discussion

Abundance of snails

The current study aimed to deepen our understanding of the variation of freshwater snail populations in central Côte d’Ivoire in the face of the construction and operation of a small, multipurpose dam. We observed a considerable increase in the abundance of snails during the second observation period, i.e. after the dam had been filled. The diversity of freshwater snails and the exponential growth of Bi. pfeifferi are probably explained by a more stable hydrological system [23]. All the snails collected belonged to the same genera and species that have been reported before in the greater Bouaké area [24] with the exception of Physa acuta that had not been reported before. Bu. truncatus was present at the level of the dam reservoir but absent in the other villages having water supply points and being drained completely during the dry season. Bu. truncatus is a cosmopolitan species with a preference for sunlight, clean, stagnant and permanent aquatic environments [19]. The construction of a multipurpose dam and formation of a small man-made lake support the proliferation of Bu. truncatus. In a preceding study by Poda in Burkina Faso it was noted that dams account for 61.7% of the biotopes with Bu. truncatus and seem the preferential habitats of this species [8]. This observation is similar to that described in our context. In contrast, Bu. globosus prefers cluttered areas and low water flow such as in an irrigated area [25, 26].

Cercarial shedding and schistosomiasis transmission

In spite of very high abundance of snails and prolonged exposure (up to 1 month) to check for cercarial shedding, none of the snails collected shed cercariae and the schistosome infection level among school children and adults was low. Indeed, with a Schistosoma infection prevalence below 10%, all the localities surveyed are considered hypoendemic [27]. This observation suggests that the high abundance of intermediate host snails does not correlate with human infection. These results are consistent with other studies from endemic areas in Uganda and Kenya; showing a high abundance of snails but no or only very few snails shedding cercariae [28, 29]. Indeed, the quasi-absence of cercariae shedding might explain the low human prevalence. The absence of infection might be due to health education received by parents and children, who emphasised avoidance of water contact such as bathing, washing clothes or kitchen utensils in the newly formed water resource. The surveys undertaken confirmed the low prevalence observed. Hence, it is conceivable that there was no local transmission of schistosomiasis at the time of the study despite suitable snail habitats. The few infected people might have acquired their infections elsewhere.

S. mansoni was rarely found in the study area. This result is consistent with observations made before in villages in close proximity to large dams, namely Lake Kossou and Lake Taabo. However, within a few years of construction of these two large dams, there were outbreaks of S. haematobium, prevalence increased from 14% to 53% and from 0% to 73% in the two dams, while S. mansoni was absent or present at very low rate [14]. Our study confirms that Central region of Côte d’Ivoire continues to have active transmission of S. haematobium. The fall of the prevalence of schistosomiasis in all the study localities might be associated with the absence of indigenous transmission and the treatment of diagnosed cases. Of note, all positive individuals were treated with praziquantel (40 mg/kg), which, according to WHO, results in cure rates ranging between 60% and 90% for Schistosoma infection [30, 31].

Our study illustrates the complex interactions between dam constructions, snail ecology and schistosomiasis transmission. Therefore, before any dam construction and throughout the life course of such water resources development projects, malacological and epidemiological survey must be implemented to continuously evaluate potential risks. Integrated control measures, including information, education and communication (IEC), environment management and access to treatment must be considered. Control and preventive measures that are readily tailored to specific settings are necessary to keep human infections and morbidity low.

Conclusions

The construction and operation of a small, multipurpose dam in Raffierkro in central Côte d’Ivoire is the likely cause of a high increase of intermediate host snail fauna. Bi. pfeifferi was the prominent intermediate host of schistosomiasis, followed by Bu. truncatus and Bu. globosus. In spite of the presence of dam and the high abundance of intermediate host snails, no evidence of local transmission of schistosomiasis was observed. Hence, adequate control and preventive measures in this context by IEC, and rigorous surveillance is necessary, so that early signs of emergences can be addressed by public health measures.