The Prawn Macrobrachium vollenhovenii in the Senegal River Basin: Towards Sustainable Restocking of All-Male Populations for Biological Control of Schistosomiasis

Early malacological literature suggests that the outbreak of schistosomiasis, a parasitic disease transmitted by aquatic snails, in the Senegal River basin occurred due to ecological changes resulting from the construction of the Diama dam. The common treatment, the drug praziquantel, does not protect from the high risk of re-infection due to human contact with infested water on a daily basis. The construction of the dam interfered with the life cycle of the prawn Macrobrachium vollenhovenii by blocking its access to breeding grounds in the estuary. These prawns were demonstrated to be potential biological control agents, being effective predators of Schistosoma-susceptible snails. Here, we propose a responsible restocking strategy using all-male prawn populations which could provide sustainable disease control. Male prawns reach a larger size and have a lower tendency to migrate than females. We, therefore, expect that periodic restocking of all-male juveniles will decrease the prevalence of schistosomiasis and increase villagers' welfare. In this interdisciplinary study, we examined current prawn abundance along the river basin, complemented with a retrospective questionnaire completed by local fishermen. We revealed the current absence of prawns upriver and thus demonstrated the need for restocking. Since male prawns are suggested to be preferable for bio-control, we laid the molecular foundation for production of all-male M. vollenhovenii through a complete sequencing of the insulin-like androgenic gland-encoding gene (IAG), which is responsible for sexual differentiation in crustaceans. We also conducted bioinformatics and immunohistochemistry analyses to demonstrate the similarity of this sequence to the IAG of another Macrobrachium species in which neo-females are produced and their progeny are 100% males. At least 100 million people at risk of schistosomiasis are residents of areas that experienced water management manipulations. Our suggested non-breeding sustainable model of control—if proven successful—could prevent re-infections and thus prove useful throughout the world.


Introduction
Schistosomiasis is a chronic parasitic disease caused by blood flukes of the genus Schistosoma, which are dependent on two hosts to complete their life cycle, an intermediate host (a freshwater snail) and a definitive host (a vertebrate). The adult parasites can live for decades and cause increasing damage to organ tissues (bladder, liver or intestine) and can result in mortality of the host [1]. One of the most heavily infected areas in the world is the Senegal River basin in which the outbreak of the disease was reported following the construction of the Diama dam, ,50 km from the mouth of the river, in 1986. The dam is a saltwater barrier and was built to support agricultural expansion in the delta and upriver by preventing saltwater intrusion during the dry season [2]. As a result of dam construction, the Senegal River basin ecosystem experienced major changes, such as habitat expansion for fresh water species, like aquatic snails hosting schistosomiasis [3][4][5][6]. Since the appearance of the dam, rates of Schistosoma haematobium infection have risen from 0-3.6% to 11.5%, and from 10.4-27.2% to 51.6% in different areas of the river basin [7]. Moreover, while S. mansoni was absent in the river basin before the construction of the dam, it was first reported 18 months after the dam was completed, with the associated infection rates now reaching up to 71.8% in some villages [7]. The ecological changes related to the separation of the upriver region from the estuary also are unfavorable for catadromous species, such as the native river prawn Macrobrachium vollenhovenii.
M. vollenhovenii is a decapod crustacean belonging to the Palaemonidae family, endemic to the west coast of Africa from the Senegal River in the north to Angola in the south [8][9][10]. The northern habitat border of the prawn, the Senegal River basin, supported artisanal prawn fishery extending from the coast to more than 400 km inland prior to dam construction [11]. This natural habitat was confronted with an insurmountable challenge following construction of the dam due to the prawn's dependence on brackish water and access to the estuary to complete their life cycle. Ovigerous females of this species must migrate to the estuary in order to release their larvae, which in turn complete their larval development period in brackish water before migrating upriver as post-larvae [12][13][14]. The increased snail numbers after construction of the dam could be explained by a slowing of the river flow and decreased saltwater intrusion, thereby expanding regions of suitable habitat for the snails. This, together with the human migration seeking employment in the expanded rice and sugar cane fields of the new agricultural zone, resulted in a spread of schistosomiasis (bilharzia) among human populations living or working upriver of the Diama dam [4,5,15]. Chemotherapy-based campaigns using praziquantel, the primary drug used today to fight schistosomiasis, have been carried out by the Senegalese government. However, to eliminate the disease, an integrated management program is required. While praziquantel effectively kills adult worms inside the definitive host's body, rapid reinfection can occur upon re-exposure to cercariae from infected snails in the environment. [16][17][18].
Snail population abundance and distribution are mediated by predators in several aquatic systems [19][20][21][22]. Accordingly, Macrobrachium rosenbergii, the most commonly aquacultured freshwater prawn in the world [23], is an effective predator of medically important freshwater snails under laboratory conditions [24][25][26]. Similarly, due to its relatively large size and tendency to consume medically important snails, M. vollenhovenii has been proposed both as a candidate for commercial aquaculture [27][28][29] and as an agent for biological control of schistosomiasis [25]. Indeed, M. vollenhovenii prawns were successful in controlling schistosome-susceptible snail populations under laboratory conditions [25]. Like other freshwater prawns, M. vollenhovenii exhibits clear sexual dimorphism, with males achieving larger maximum size than females [30][31][32]. Sexual dimorphism in many crustaceans is mediated by secretions of the androgenic gland (AG), a masculinizing endocrine organ unique to this sub-phylum [33][34][35][36]. The masculinity-regulating hormone secreted by this gland in decapod crustaceans is the insulin-like hormone of the androgenic gland (IAG). The gene encoding the hormone is uniquely expressed in males, with the function of the protein having been studied in several species [37][38][39][40]. Following discovery of the AG in M. rosenbergii [41], a full functional sex reversal was achieved by bilateral ablation of the gland [42,43]. The discovery and sequence of the IAG-encoding gene in M. rosenbergii (Mr-IAG) [44] opened a path for the development of an innovative method of sex reversal through temporal RNA interference (RNAi) using double-stranded Mr-IAG RNA [42,45]. In this manner, sex reversed males (neo -females) are created that, when crossed with normal males, produce all-male progeny. Since male prawns grow faster than females and reach a larger size, these findings were translated into a commercialized biotechnology, namely the first use of RNAi in aquaculture, initially applied for the production of all-male prawn populations [46]. We hypothesized that the same could be achieved with other Macrobrachium species, such as M. vollenhovenii.
In this multi-disciplinary study, we assessed the current abundance of M. vollenhovenii prawns in the Senegal River basin through capture using baited prawn traps. Such trapping efforts were supplemented by collaboration with local fisherman via a program offering purchase of their prawn catches throughout the course of the study period. We also conducted retrospective interviews with fishermen regarding the abundance of prawns along the Senegal River basin before and after construction of the Diama Dam. Studies of prawn catches and earlier literature on male superior size [31,32] suggested that both prawn fisheries and their biological control functions could benefit from restocking with all-male populations. A further objective of this study was thus to lay the required molecular foundation for the production of all-male populations. Accordingly, we characterized the AG and the IAG-encoding gene of M. vollenhovenii as a first step towards producing all-male populations for mass restocking of biological control agents.

Monitoring prawn abundance in the Senegal River basin
To monitor the current abundance of prawns upstream of the Senegal River basin, 2-4 large crayfish traps were placed for 17-24 hours per site-visit at 15 sites throughout the lower Senegal River basin (Fig. 1B, marked with white and grey stars). Sites were visited bimonthly between February, 2011 and June, 2012. The traps used were commercial cylindrical crayfish traps constructed of a collapsible metal frame 30 cm in diameter and 60 cm in length, surrounded by fishing-net material. Traps were equipped with bait (either dead fish or meat plus vegetables, such as cassava root or local plant material, as recommended by local prawn fishermen). The traps and baits were tested in 9 m 2 prawn tanks at the Senegalese National Aquaculture facility prior to deployment and were found to successfully capture prawns within a few hours.
To compare the abundance and distribution of prawns upstream of the Diama Dam in the Senegal River basin with abundance in the vicinity of the Diama Dam, prawns were purchased from local fisherman. All M. vollenhovenii prawns used for the present study were collected from September 12, 2012 to August 31, 2013 (excluding April and July, 2013, due to budgetary obstacles) by a group of six fishermen who work regularly both upand downstream of the Diama Dam (Fig. 1A). All prawns caught by fisherman were captured near the Diama Dam in the Saint-Louis region, Senegal (N 16u12952,650 W 25u20916,070, marked as ''Fisherman's location'' in Fig. 1A). The fishermen used

Author Summary
Schistosomiasis is a chronic parasitic disease that infects millions of people, especially in Africa. Schistosomes are transmitted by direct contact with water sources infested by freshwater snails, which are intermediate hosts for the parasite. The cure in humans is a drug, praziquantel, that kills the mature parasites inside the human body. The main problem with controlling the parasite by drug treatment is the high re-infection rate, since individuals are in contact with infected water on a daily basis. To efficiently combat the disease, an integrated management program is needed that includes control of infection in the intermediate host snails. We suggest the use of non-migrating, allmale populations of freshwater prawns that efficiently prey on these snails. Here, we describe the case of the Senegal River basin as an example of human actions (dam construction) that resulted in severe ecosystem changes, including exclusion of the native river prawns and expansion of snails hosting schistosomiasis. We have conducted an interdisciplinary study that documents the reduction of prawn abundance in the Senegal River and lays the molecular foundation for technology to produce all-male prawn populations to be used as part of an integrated disease control program, including both periodic stocking of juvenile prawns and chemotherapy.
three types of fishing techniques, including baited traps (60 cm high, 80 cm diameter, made of metal and covered with fishing net), ''sleeping nets'' (20066 m nylon net, 36 mm mesh with a 2 mm string) and a ''drifting net'' (same material as the sleeping net). The drifting nets are built of three nets attached together (60066 m), so as to cover the width of the river.
Since little quantitative information on prawn abundance in the past was available for this study, attempts to compare current abundance with the situation before construction of the dam relied on retrospective interviews with fishermen in villages along the Senegal River (Fig. 1B, marked with black stars). This complementary approach included a standard questionnaire (see supplemental appended item S1) designed to solicit information on the prawn catch today, compared to the past. The fishermen were asked twenty questions, including verification of their fishing experience (years of activity) and whether fishing is their primary activity (in order to estimate their reliability). Fishermen were shown pictures of M. vollenhovenii to confirm or reject prior recollection of the prawns by appearance. Locations where both trapping and interviews were conducted are marked with grey stars on the map in Fig. 1B. Non-parametric statistical analysis was conducted to compare the reported abundance of the prawns before the construction of the dam and today in five villages upstream of the dam. Concomitant with the decline in prawn abundance, the number of active fishermen in the five villages, was reported by the fishermen to have declined from 175 before construction of the dam to only 18 today that were approached. Of these, the five who were active before construction of the dam and remain active today were selected for the study (one from each village).

Statistical analysis of weight comparisons between males and females
To examine the relationship between sex and body weight, a two-sample Kolmogorov-Smirnov test, comparing the data distribution of both sexes, was initially conducted. An R6C test of independence was then performed to determine whether there was a dependency between sex and body weight, relying on the frequency of males and females weighing above 100 g. All analyses were conducted using STATISTICA 10 (StatSoft software, Tulsa, OK).

Molecular studies
All Prawns used in the molecular study were anesthetized on ice for 5 min prior to dissection. Species determination was based on a molecular analysis using PCR for amplification of M. vollenhovenii mitochondrial 16S rRNA sequence (GenBank accession numbers see Table 1.). RNA samples from animals caught by the fishermen (see ''Monitoring prawn abundance in the Senegal River basin'') were extracted and cDNA was prepared for PCR amplification as previously described [47]. For PCR amplification, the forward and reverse primers listed in Table 2 were used. PCR products were separated on agarose gels and bands were excised, purified and cloned as previously described. Sequences were obtained and compared to the known sequences using the BLAST algorithm.
RT-PCR and M. vollenhovenii insulin-like androgenic gland hormone (Mv-IAG) tissue specificity. To enable easier identification of the AG, an endocrine manipulation of bilateral eyestalk ablation, causing hypertrophy of the AG (hAG), was performed on three mature males, as previously described [39]. Dissected AGs were placed in RNA SAVE (Biological Industries, Beit Haemek, Israel) and transported for molecular analysis at Ben-Gurion University, Beer-Sheva, Israel. RNA from the hAG of an endocrinologically-manipulated male caught by the fishermen (see ''Monitoring prawn abundance in the Senegal River basin'', manipulation described above) was extracted and cDNA was prepared as described above. The cDNA was then amplified by PCR, as previously described [44], using specific forward (nt 627-646) and reverse (nt 770-789) primers based on the sequence of Mr-IAG. M. rosenbergii b-actin (Table 1) served as a positive control using appropriate forward and reverse primers. PCR products were cloned and sequenced.
Tissue specificity was determined by PCR using cDNA prepared from several mature animal tissues (AG, ovary and hepatopancreas), as described above. The cDNA was then amplified by PCR using specific Mv-IAG forward (nt 310-334) and reverse (nt 589-611) primers. M. rosenbergii b-actin served as a positive control [44]. All primers used in these studies are listed in Table 2.
Sequencing Mv-IAG and bioinformatics analysis. The sequences of the 59 and 39 ends of Mv-IAG were obtained by 59 and 39 rapid amplification of cDNA ends (RACE) using the SMARTer RACE kit (Clontech) following the manufacturer's protocol. PCR amplification of the 59 region was achieved using the gene-specific reverse primer from the 39 Race kit, (nt 108-132) and the Universal Primers Mix (UPM) provided with the kit. PCR amplification of the 39 region was performed with the UPM as a reverse primer and the gene-specific forward primer (nt 297-322). The PCR products were cloned and sequenced as described above. Following determination of the full sequence of Mv-IAG, a multiple sequence alignment, including its deduced peptide, was conducted using the CLUSTAL W algorithm and IAG sequences  Table 1) and an insulin protein from Caenorhabditis elegans as an out-group. Evolutionary history was inferred using the Neighbor-Joining method [49]. The bootstrap consensus tree inferred from 5,000 replicates was taken as representing the evolutionary history of the selected mature IAGs among the taxa analyzed.

Histology and immunohistochemistry
AGs were dissected from mature males, together with the attached terminal ampullae, under laboratory conditions in Senegal. Tissue samples were fixed in modified Carnoy's II for 72 h while being transported to Ben-Gurion University, Israel, where they were further processed according to conventional procedures. Five mm-thick sections were prepared. One out of five consecutive slides was stained by hematoxylin and eosin as previously described [47].The other four slides were analyzed by immunohistochemistry using rabbit a-rec-Mr-IAG antibodies (1:1500) as previously described [50].

Results
Presence of M. vollenhovenii in the Senegal River basin M. vollenhovenii trapping in the Senegal River basin. In the survey of current prawn abundance in the Senegal River basin, only three adult prawns (two of them Macrobrachium vollenhovenii and one Atya sp.) were trapped over a 16-month span corresponding to a total of 6,297 trap-hours of effort. The two M. vollenhovenii prawns were captured in the vicinity of Diama Dam, one upstream of the dam and the other downstream (black circles in Fig. 1A). In addition, juvenile Macrobrachium prawns (identified to genus only -adult specimens are required to identify species) were encountered below the dam, but not above. At the other thirteen upstream locations (white and grey stars in Fig. 1B), no Macrobrachium spp. prawns were captured despite 5,354 traphours of effort. A total of 359 fish, 40 crabs and one turtle were caught in traps during the same surveys.  Fig. 2A. The distribution of the prawns caught upstream or downstream of the dam varied throughout the year. According to fishermen, between June, 2012 and January, 2013, about 80% of the prawns were collected downstream of the dam, and 20% upstream, near Diama village (based on reported retrospective estimates relying on the fishermen's recall over the survey period, Fig. 1A). However, between February and May, 2013, the trend was the opposite, with 80% of the prawns reported to be caught upstream.
Comparing the average and maximal weights of males versus females (Fig. 2B) indicated that in most cases, the average weight of males was greater. More noteworthy were the maximal weights recorded from the three largest male or female specimens, which indicated that males could achieve a much larger maximal weight. Histograms depicting male and female weights show a bi-modal frequency distribution (Fig. S2) that divides the male population into two different weight groups, namely 0-100 and 100-240 g. When considering 100 g or more as a 'large' specimen, a significant pattern of sex dependency was found, with 17.7% of the males being 'large' versus 1.4% of the females (x 2 1 = 20.07, P, 0.001). Thus, our data suggest that males reach larger weights than females, especially during the wet season (June to September, reported as the best time to fish for prawns). The largest female encountered during the study weighed 129 g, as opposed to 235 g for the largest male.
Interview survey of fisherman from the Senegal River basin. Retrospective comparison of the current prawn abundance with the situation before dam construction reflected a dramatic decrease in the reported catch after the Diama Dam was constructed. Five fishermen from five different locations upstream of the Diama Dam (Fig. 1B) were approached with a retrospective questionnaire (see supplementary material S1). All claimed to have caught prawns routinely before the dam was built, whereas today only a very small prawn catch was claimed. If caught, the maximum quantity of prawns captured, as reported by the fishermen, was significantly lower than quantities reported from the time before construction of the dam (Table 3, T = 0.00, P = 0.04, Wilcoxon matched pairs test). All of those interviewed have been active fisherman for at least 45 years and are thus firsthand witnesses of the dam construction event.
The full-length cDNA of Mv-IAG: Encoding sequence and deduced peptide, multiple sequence alignment with decapod IAGs and phylogenetic analysis Due to the above size/weight differences found between M. vollenhovenii males and females and the notion that restocking with an all-male population will be advantageous, the AG and hormone that mediate maleness in this species were studied. Fulllength Mv-IAG cDNA was found to be 1,213 bp-long (Fig. 3A, Accession number KJ524578). The sequence was isolated from a hAG by means of RT-PCR using Mr-IAG-based primers, followed by 59   The predicted Mv-IAG ORF encodes a preprohormone, a signal peptide, the B chain, the C peptide, and the A chain in linear order (Fig. 3B). The B and A chains of Mv-IAG are thought to be connected by two putative inter-chain disulfide bridges formed between Cys12 and Cys23 residues of the B chain and Cys15 and Cys32 of the A chain. Two other cysteine residues located in the A chain, Cys14 and Cys23, are suggested to form an  intra-chain disulfide bridge. Two putative cleavage sites of RR and KR at amino acids 69 and 129, flanking the C peptide were joined to the B and A chains, respectively. The Mv-IAG sequence was compared with those from four other decapod crustacean species (M. rosenbergii, P. pelagicus, C. quadricarinatus and F. chinensis) in a multiple sequence alignment (Fig. 4). The positions of twenty amino acids were conserved. These included six cysteine residues, with two found in the B chain and four in the A chain. A phylogram generated using neighborjoining methods [49] segregated the different decapod IAGs in accordance to their genus (Fig. 5). Protein INS-1 of C. elegans was used as an out-group to all of the twelve decapod IAGs known to date. It is clear that Mv-IAG is more related to Mr-IAG than to any other sequence. The different clades in the phylogram, reflecting the similarities of the proteins in the different species, were found to correlate with taxonomic relations in the cases of the Macrobrachium, the Palaemon and the Cherax species.
Localization of the AG, Mv-IAG tissue specificity at the transcript and protein levels The AG is located next to the sperm duct (Fig. 6 middle). The sperm duct wall is rich in muscle fibers and filled with mature spermatozoa (Fig. 6 left). Mv-IAG transcription was demonstrated by RT-PCR of cDNA from the AG but not from the male hepatopancreas or female ovary. The M. rosenbergii housekeeping gene b-actin served as a positive control (Fig. 7).
Based on immunohistochemical analysis, Mv-IAG was localized to hAGs (Fig. 8), using rabbit anti-Mr-IAG specific antibodies [50]. A specific signal was observed only in the cytoplasm of the AG cells (Fig. 8A), as nuclei were only stained by DAPI and not by the antibodies (Fig. 8B). The specificity of the anti-Mr-IAG antibodies was further validated when no signal could be observed upon incubation of normal rabbit serum with the AG sections (Fig. 8C). Sections were also stained with DAPI, which enabled nuclear localization as negative controls (Fig. 8D).  The degree of conservation is presented by the dots under the columns. One dot represents less conserved than two dots, while an asterisk indicates identity. The most conserved feature is the backbone consisting of six cysteine residues (boxed) which gives rise to disulfide bridges (lines connecting the boxes). doi:10.1371/journal.pntd.0003060.g004

Discussion
Early malacological literature suggests that the outbreak of schistosomiasis in the Senegal River basin occurred due to ecological changes resulting from the construction of the Diama and Manantali Dams, which were completed in 1986 and 1990, respectively [4,6,15]. Our current surveys in the Senegal River basin, including retrospective information from fishermen, appear to confirm the notion that the abundance of M. vollenhovenii was negatively influenced by construction of the Diama Dam. Although the historical, interview-based data could not be confirmed with independent fisheries or catch data prior to the appearance of the dam, research has consistently shown fishermen's knowledge to be a reliable estimate of relative abundance and distribution of fished species [51,52]. Moreover, during the present study, fishermen in the Diama Dam region received an incentive to fish M. vollenhovenii in the form of a reward offered by the current project. This presented yet further evidence supporting the reduction in abundance reported by fishermen as these individuals now devoted considerable effort to the prawn catch. Still, despite the increased effort, the data collected were comparable to those reported in the interviews. However, the causal relationship between prawn scarcity and the increased abundance of the snails and schistosomiasis infections upriver of the Diama Dam could not be established using our correlative data and should be further investigated.
The use of prawns as biological control agents has been suggested and tested with both M. rosenbergii and M. vollenhovenii, showing that freshwater prawns are effective predators of schistosome-susceptible snails under laboratory conditions   [24][25][26]. The novel approach of restocking populations of an indigenous prawn for its biological control abilities could become a powerful complement to chemotherapy campaigns. Today, campaigns for the distribution of this drug focus on periodic administration of the anthelminthic, praziquantel, to kill the adult worms [53]. What is lacking is a sustainable control strategy to prevent re-infection from snail to man [16,54]. The ability of an invasive, non-native crustacean to eliminate snails was shown in  Kenya, with a concomitant reduction of prevalence and intensity of urinary schistosomiasis in school children [55]. To the best of our knowledge M. vollenhovenii is the first indigenous crustaceanpredator proposed for such purposes. Our study suggests a strategy of restocking all-male prawns at a significant scale in the Senegal River basin involving a population that could be bred, hatched, and nurtured to the post-larval or juvenile stage in aquaculture facilities and then released into schistosomiasis transmission foci. If all-male prawn populations show an advantage in terms of yield and biological control effectiveness in the field, this strategy could have broad application in West African public health, fisheries and aquaculture sectors. Moreover, RNAi has been demonstrated to be a potent method for temporal gene manipulation in crustaceans [56] and indeed, a sexual shift has been achieved in all cases of IAG RNAi in crustaceans tested thus far [45,57]. Furthermore, the present study shows the high similarity between the IAG of the African prawn and that of other species, including that species in which RNAi has been successfully performed. Results of the present study also suggest that male M. vollenhovenii prawns reach larger sizes than females, as has been reported in the past [31]. Thus, the strategy of monosex culture could prove advantageous, similar to the proven production advantages of such cultures in M. rosenbergii aquaculture. These proven aquaculture benefits include the faster growth rate of males [13,43,58], the ability to selectively harvest non-growing large males in order to stimulate a growth spurt in the subordinate morophtypes [59][60][61], and the premium market prices acquired by large specimens [30,62]. All of these advantages also apply to the sustainable restocking of prawns for biological control of snails. Because there is a need to ensure that the prawns will feed within specific, snail-infested sites, it is logical to use all-male nonmigrating agents, as suggested with other Macrobrachium species [12,14].
The sustainability of the solution proposed here will depend on a fisheries policy encouraging the harvesting or culling of the largest dominant males in order to boost the growth of smaller males and to maximize yields, as is routinely done in prawn aquaculture [63]. Such a policy will enable avoidance of overpopulation of the river since the size of the population will depend on the ratio between stocking and fishing rates. Moreover, since different-sized prawns have been found to be differentially efficient in snail predation [25], a continuous restocking with younger, fastgrowing male prawns will also support the biological control task.
To achieve the all-male cohorts desired for restocking and fisheries, the current biotechnology relies on molecular manipulation of the IAG [46]. Here, we characterize M. vollenhovenii AG and IAG as a first step towards the ultimate goal of enabling routine, all-male M. vollenhovenii culture via recently established temporal RNAi-based biotechnology [46]. M. vollenhovenii IAG, has been completely sequenced in the present study and was found to share high similarity with homologous molecules in other decapod crustaceans [44,47,64]. Mv-IAG contains all the components of an insulin family member [38]. The M. vollenhovenii AG is anatomically and histologically similar to that described in M. rosenbergii [44]. Of the known decapod IAGs, Mv-IAG had the highest similarity to the IAG of its congener, M. rosenbergii (85% identity). Immunohistochemical analysis using anti-Mr-IAG antiserum demonstrated the presence of Mv-IAG in the cytoplasm of AG cells. The high sequence similarity of Mv-IAG and Mr-IAG, as shown by bioinformatics tools in this study, provided the lead to pursue what turned out to be a successful use of anti-Mr-IAG antibodies to localize Mv-IAG in immunohistochemistry.
Based on our results and the high similarity of M. vollenhovenii to M. rosenbergii, it is realistic to assume that the biotechnology proven to be effective for mass production of M. rosenbergii allmale populations in prawn aquaculture [46] can be directly implemented to the production of all-male M. vollenhovenii populations.
At least 90% of the 243 million people currently infected with schistosomiasis in the world are in Africa [1] and at least 100 million of the more than 700 million people at risk of infection reside in areas that experienced major water management manipulations (i.e. dams and irrigation schemes), as was the case in the Senegal River basin [4,7]. A meta-analysis [7] found that schistosomiasis risk in Africa was doubled for people living near dams and irrigation schemes, compared with people far from these schemes. Our suggested sustainable model of control, namely restocking native all-male prawn populations in the Senegal River using aquaculture and biotechnology, both as biological control agents and as an augmented fisheries crop, if proven successful locally, could be useful at other locations throughout the west coast of Africa where M. vollenhovenii is native (Fig. 1C) and where they may have been recently extirpated by dams. It is noteworthy that the use of all-male populations could permit responsible and sustainable restocking in other regions of Africa where these prawns are non-native, given that they have little invasion risk because the all-male prawns cannot revert to females and, therefore, cannot reproduce.