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      Precision mapping of snail habitat provides a powerful indicator of human schistosomiasis transmission

      research-article
      a , 1 , b , b , b , c , d , d , e , f , a , g , h , i , a , j , k , l , k , l , k , l , l , m , n , n , n , n , n , o , n , b
      Proceedings of the National Academy of Sciences of the United States of America
      National Academy of Sciences
      bilharzia, ecological levers for infectious disease control, snail control, spatial ecology, urogenital schistosomiasis

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          Significance

          Schistosomiasis is a parasitic disease that affects ∼206 million people globally. The World Health Organization recently endorsed control of the freshwater snails that host schistosome infectious stages, and here, we show how to better target those snail control efforts. Schistosomiasis infection occurred on a local scale at our study sites in northwestern Senegal, suggesting that small-scale interventions can suppress transmission. However, snail clusters were so ephemeral that attempts to target them for removal would be inefficient. Instead, we found easy-to-measure environmental proxies that were more effective than snail variables at predicting human infections, including area of snail habitat within the site and total site area. Our work indicates that satellite- or drone-based precision mapping could efficiently identify high-transmission areas.

          Abstract

          Recently, the World Health Organization recognized that efforts to interrupt schistosomiasis transmission through mass drug administration have been ineffective in some regions; one of their new recommended strategies for global schistosomiasis control emphasizes targeting the freshwater snails that transmit schistosome parasites. We sought to identify robust indicators that would enable precision targeting of these snails. At the site of the world’s largest recorded schistosomiasis epidemic—the Lower Senegal River Basin in Senegal—intensive sampling revealed positive relationships between intermediate host snails (abundance, density, and prevalence) and human urogenital schistosomiasis reinfection (prevalence and intensity in schoolchildren after drug administration). However, we also found that snail distributions were so patchy in space and time that obtaining useful data required effort that exceeds what is feasible in standard monitoring and control campaigns. Instead, we identified several environmental proxies that were more effective than snail variables for predicting human infection: the area covered by suitable snail habitat (i.e., floating, nonemergent vegetation), the percent cover by suitable snail habitat, and size of the water contact area. Unlike snail surveys, which require hundreds of person-hours per site to conduct, habitat coverage and site area can be quickly estimated with drone or satellite imagery. This, in turn, makes possible large-scale, high-resolution estimation of human urogenital schistosomiasis risk to support targeting of both mass drug administration and snail control efforts.

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          Performance of several variable-selection methods applied to real ecological data.

          I evaluated the predictive ability of statistical models obtained by applying seven methods of variable selection to 12 ecological and environmental data sets. Cross-validation, involving repeated splits of each data set into training and validation subsets, was used to obtain honest estimates of predictive ability that could be fairly compared among methods. There was surprisingly little difference in predictive ability among five methods based on multiple linear regression. Stepwise methods performed similarly to exhaustive algorithms for subset selection, and the choice of criterion for comparing models (Akaike's information criterion, Schwarz's Bayesian information criterion or F statistics) had little effect on predictive ability. For most of the data sets, two methods based on regression trees yielded models with substantially lower predictive ability. I argue that there is no 'best' method of variable selection and that any of the regression-based approaches discussed here is capable of yielding useful predictive models.
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            To Explain or To Predict?

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              Bidirectional Introgressive Hybridization between a Cattle and Human Schistosome Species

              Introduction The increasing use of molecular techniques in ecological studies has revealed many cases of hybridization and introgression in plants and animals [1]–[3], but examples in metazoan parasites are rare [2]. Hybridization can have a major impact on adaptive radiation and diversification of the species under study [2],[4], and in the case of parasites, this may also have an impact on the host and the epidemiology of disease. The acquisition of new genes may generate new phenotypes that might differ in virulence, resistance, pathology, and host use, ultimately leading to the emergence of new diseases. Schistosomiasis is a disease of medical and veterinary importance in tropical and subtropical regions, caused by parasitic flatworms of the genus Schistosoma (subclass Digenea). Over 200 million people are infected, of which 85% live in Africa. Chronic infection may lead to severe liver, intestinal and bladder complications, sometimes leading to death. Schistosoma species have a two-host life cycle with an asexual stage within an intermediate freshwater snail host and a sexual stage within the definitive mammalian host; parasite eggs are voided in the urine or faeces depending on the species. Schistosomes are highly unusual trematodes as they are dioecious, which creates an opportunity for interplay between male and female parasites in the vasculature system of the definitive mammalian host. Several crossing experiments have been carried out in controlled laboratory settings especially between species belonging to the Schistosoma haematobium group (e.g. [5]–[7]). Depending on the phylogenetic distance between the two species involved, crossing may lead to parthenogenesis or hybridization, with certain combinations being more viable than others. Experimental hybrids tend to show heterosis: they have a higher fecundity, faster maturation time, higher infectivity, and wider intermediate host spectrum compared to their parental species (e.g. [7],[8]). In nature, the distribution of schistosome species and their intermediate snail hosts, together with definitive host specificity are believed to restrict these hybridization events from occurring. However, both natural (climate change) and anthropogenic changes (migration, deforestation, water development) can break down the ecological isolation barriers by facilitating the introduction of parasite species and strains into new areas, resulting in novel host-parasite and parasite – parasite interactions. For example, deforestation of the tropical rainforest in Loum (Cameroun) led to the establishment of the snail B. truncatus, the intermediate host of S. haematobium. Shortly after, the parasite S. haematobium became established. The epidemiology of schistosomiasis changed dramatically: prevalences and infection intensities increased and a complete switch from intestinal schistosomiasis (S. guineenis) transmitted by B. forskalii to urinary schistosomiasis (S. haematobium and the hybrid S. haematobium×guineenis) was observed [9],[10]. The extent of hybridization only became clear after the application of molecular genetic markers including SSCP and sequence analysis [11]. Other examples of hybridization events that came to light through molecular studies include the hybridization of a primarily human parasite, S. mansoni and a rodent parasite S. rodhaini in western Kenya [12],[13]. In this example, hybrid cercariae have been recorded from naturally infected Biomphalaria snails, but transmission of these hybrids into humans has not been detected. Because of their inaccessibility in the human mesenteric system, it is very difficult to obtain adult schistosome worms. Traditionally, schistosome infections were identified by egg morphology, site of infection and snail compatibility studies but these methods are not sufficiently sensitive and interactions between species can be missed. Laboratory passage of natural miracidia into adult worms enabled the development of molecular techniques but this labour-intensive technique has a low success rate and leads to artificial selection of specific parasite genotypes [14]. The recent development of a storage protocol for larval schistosomes on Whatman FTA® Cards [15] together with new molecular markers have provided tools to genotype individual miracidia and cercariae sampled directly from the field. The initial project aim was to perform a large molecular genotyping study of human schistosomes in northern Senegal to study the population structure and transmission dynamics of Schistosoma species. The habitats found in the Senegal River Basin (SRB) have changed dramatically over the last 30 years due to the construction of the Diama Dam, intended to prevent salt-water intrusion from the sea facilitating rice and sugar cane agriculture, and the Manantali Dam in Mali, constructed for hydroelectricity and regulation of water flow. The subsequent ecological changes (e.g pH and salinity) together with increased irrigation created new aquatic habitats, which allowed the prolific spread of Biomphalaria pfeifferi, the intermediate host of S. mansoni, and various species of Bulinus responsible for transmitting S. haematobium and S. bovis. This resulted initially in a major outbreak of human intestinal schistosomiasis (S. mansoni) [16],[17] followed by subsequent dynamic changes in the prevelance of both urinary (S. haematobium) and intestinal schistosomiasis (Polman, unpublished data). Several areas of sympatry between these schistosomes now exist, and many children can be found with both urinary and intestinal schistosomiasis. It is likely that the prevalence of the bovine schistosomes, especially S. bovis, has also increased, but this has not been documented. Both the laboratories of the Natural History Museum and the Institute of Tropical Medicine involved in the studies discovered independently the occurrence of schistosome miracidia from children with a S. bovis mitochondrial genetic profile. In 1970, Taylor demonstrated the successful experimental hybridization of S. haematobium and S. bovis while Brémond et al. [18] found schistosome species in Niger with allozyme profiles that were intermediate between S. bovis and S. haematobium or S. curassoni, but more sensitive markers were needed to discriminate S. haematobium from S. curassoni. In this study we use molecular sequencing tools to provide conclusive evidence of the hybridization of S. haematobium and S. bovis in nature, with hybrid offspring infecting children in northern Senegal. This study provides a first glimpse at the intricacies between a human and a cattle schistosome species and our data are discussed in relation to implications for schistosomiasis epidemiology and control. Results Nuclear and mt DNA genotyping Sequence identification cox1 mtDNA (545 bp) – Pairwise distance analysis of all the sequence data (pure species, hybrids and the reference taxa) showed that there was 12% sequence divergence separating S. haematobium and S. bovis. The genetic distance between S. bovis and S. curassoni and between S. bovis and S. mansoni was 6% and 21% respectively (Table 1). No sequence variation was found within the S. haematobium sequences. 0.3% sequence divergence was found within the S. bovis sequences. Sequences of the most prevalent hybrids found in the urine and stool samples contained 3 point mutations compared to the sequences from the pure S. bovis cercariae. None of the hybrid sequences were identified as being S. mansoni or S. curassoni (Table 1). 10.1371/journal.ppat.1000571.t001 Table 1 Uncorrected pair-wise distances between the cox1 mtDNA sequences of the reference and hybrid schistosomes. 1 2 3 4 5 6 1. S. haematobium - - - - - - 2. S. bovis 0.118 - - - - - 3. S. bovis cox1 hybrid* 0.114 0.006 - - - 4. S. haematobium cox1 hybrid** 0 0.118 0.114 - - 5. S. curassoni 0.118 0.061 0.063 0.118 - - 6. S. mansoni 0.176 0.206 0.202 0.176 0.214 - Hybrids with the genetic profile: *cox1 S. bovis+ITS rRNA S. haematobium; **cox1 S. haematobium+ITS rRNA S. haematobium/S. bovis. ITS nuclear rRNA (927 bp) – S. haematobium and S. bovis differed at 5 point mutations in all specimens examined. No intra-specific variation was detected within all the ITS sequences, with the exception of hybrids 2 and 3 (Table 2). These showed additive chromatogram profiles at the polymorphic positions between the reference S. bovis and S. haematobium sequences, with the larger peak representing the S. haematobium genotype and the smaller detected peak representing the S. bovis genotype (peak difference less than 20%). 10.1371/journal.ppat.1000571.t002 Table 2 Data for the natural S. haematobium x S. bovis hybrids in northern Senegal. Location Stage From No. sequenced‡ No. hybrids Sequence identification cox1 ITS rRNA Nder Miracidia Urine 5 1 S. bovis S. haematobium Nder Miracidia Urine 5 2 S. bovis S. haematobium Nder Miracidia Urine 5 2 S. bovis S. haematobium Nder Miracidia Urine 5 2 S. bovis S. haematobium Nder Miracidia Urine 5 1 S. bovis S. haematobium Nder Miracidia Stool 5 1 S. haematobium S. haematobium+S.bovis peaks* Nder Cercariae B. globosus 49 1 S. haematobium S. haematobium+S.bovis peaks* Mbane Cercariae B. truncatus 13 4 S. bovis S. haematobium Mbane Eggs Stool• 16 3 S. bovis S. haematobium Mbane Miracidia Urine 11 2 S. bovis S. haematobium Mbane Eggs Stool 5 1 S. bovis S. haematobium Mbane Eggs Stool 1 1 S. bovis S. haematobium Gaya Eggs Stool• 4 2 S. bovis S. haematobium Thiekenne Eggs Stool 15 3 S. bovis S. haematobium Thiekenne Miracidia Urine 11 3 S. bovis S. haematobium Thiekenne Miracidia Urine 4 1 S. bovis S. haematobium Mbodjenne Eggs Stool 5 1 S. bovis S. haematobium Tiguet Eggs Stool• 5 1 S. bovis S. haematobium * At the polymorphic positions between the S. haematobium and S. bovis sequences two significant chromatogram peaks are seen. The higher one matching S. haematobium and the lower one matching S. bovis (peak heights differing less than 20%). • Pooled samples from a number of children. All other samples are from individual children. ‡ The number of individual larval stages sequenced per patient or snail infected with hybrids. Eggs and miracidia The majority of eggs and miracidia collected from the human stool and urine samples were identified as S. mansoni and S. haematobium. However, 15% of the sequenced eggs or miracidia presented a genotype suggesting a hybrid origin. Most of these had an ITS rRNA fragment that was identical to S. haematobium and a partial cox1 mtDNA fragment which was identified as S. bovis. A single miracidium (hybrid 2, Table 2) sampled from one of the human stool samples from Nder had a different composition: the cox1 fragment was identical to cox1 from S. haematobium and the ITS rRNA sequence showed double chromatogram peaks as described above. Hybrid eggs and miracidia were found in the urines and stools of 8 and 7 children respectively, in 6 different villages around Lac de Guiers and along the Lower Valley of the Senegal River Basin (Table 2). Cercariae from snails Cercariae from naturally infected intermediate snail hosts presented pure S. haematobium genotypes from B. globosus and pure S. bovis genotypes from B. truncatus. Both snail species were also found shedding cercariae that displayed the hybrid genetic profiles. One out of three infected B. truncatus snails collected in Mbane and one B. truncatus from Rhenne were shedding hybrid cercariae presenting an ITS sequence identical to S. haematobium and a cox1 sequence identified as S. bovis. In Nder, a single cercaria (hybrid 3, Table 2) isolated from B. globosus had a cox1 sequence identical to S. haematobium and an ITS sequence identified as both S. haematobium and S. bovis with double chromatogram peaks as described above. Egg morphology It was not possible to record egg morphology in the field but some limited data are available for samples from Thiekenne. Atypical and intermediate shaped eggs were found in both a pooled stool sample from 6 individual children and a stool sample from a single child. Apart from the expected lateral spined S. mansoni eggs three types of terminal spined eggs were observed: the typical S. bovis type (length ∼202 µm), the typical S. haematobium type (length ∼144 µm) and (variations of) the slender intermediate form between S. haematobium and S. bovis (length ∼174 µm), suggested to be hybrid eggs [5]. Co-infections within the definitive host All but one of the fifteen patients that were infected with hybrids were also infected with S. mansoni (median 18 epg) and S. haematobium (median 93,5 eggs/10 ml). Several children were found to be passing S. haematobium shaped eggs in their stool samples and this could indicate inter-specific mating between S. mansoni males and S. haematobium females. However most eggs appeared viable and could reflect hybridization between S. haematobium and S. bovis. Discussion Here we present conclusive evidence for the natural hybridization between the cattle parasite S. bovis and the human parasite S. haematobium. The hybrid species are able to infect humans, and they use the intermediate snail hosts of both parental species, B. globosus and B. truncatus. Our data imply that one or both of these parental schistosome species has managed to infect the definitive host of its sister species through host switching, enabling these schistosomes to interact. Back-crossing of the hybrid progeny with one of the parental species resulted in the observed introgression. Two hybrid lines have been found, resulting from bidirectional introgressive hybridization. The first line is the most prevalent one resulting from an initial cross between a male S. haematobium and a female S. bovis, leading to introgression of S. bovis mtDNA into S. haematobium. This proves that these F1 hybrids are fertile and able to reproduce. The observation of hybrid egg shapes also suggests the occurrence of further generation hybrids and or back-crossing. These data together with the few mutations in the cox1 fragment compared to the pure S. bovis sequence, indicate that this hybridization goes beyond the 1st generation, suggesting a stable ‘hybrid zone’. This is also supported by the occurrence of this hybrid over a wide geographical range, in villages separated from each other by 5–200 kilometer and located near different water resources (different tributaries of the SRB, and Lac de Guiers, see Figure 1). The other hybrid line (resulting from a cross between a male S. bovis with a female S. haematobium) is much less frequent and is most likely a first generation hybrid as suggested by the double peaks in the nuclear rRNA ITS sequences. F1 hybrids usually display both parental nuclear ITS copies, resulting in additive chromatograms [19],[20]. Biased homogenization towards one of the parental sequences can already occur in F2 hybrids or backcross generations due to concerted evolution operating in the ribosomal arrays [21] or to asymmetrical backcrossing [20]. As such, this cross might be less viable and less successful than the reverse cross. Laboratory experiments have shown that hybridization between schistosomes can be unidirectional, due to competition between males, or due to genomic incompatibility like hybrid breakdown. Taylor [5] showed that experimental crossing between male S. haematobium worms and female S. bovis worms readily occurred resulting in viable hybrid offspring but he did not test the reverse cross nor backcrosses. 10.1371/journal.ppat.1000571.g001 Figure 1 Map of the study area in northern Senegal indicating the villages where Schistosoma haematobium x S. bovis hybrids have been observed (see Table 2). Hybridization and introgression Ecological barriers between species can be lost due to both natural and anthropogenic changes. Deforestation of the tropical rainforest in Loum led to the establishment of S. haematobium followed by introgressive hybridization and competitive exclusion of the endemic S. guineensis [9],[22]. In this particular study, the habitat of the Senegal River Basin has changed dramatically over the last 30 years due to the construction of the Diama and Manantali Dams in Senegal and Mali respectively. These dams prevented salt-water intrusion from the sea and stabilized the flow, facilitating new forms of agriculture. This was followed by human population movements to these resources, increased migration of livestock and snails, creating areas for close associations between humans and domestic livestock facilitating interplay between the schistosomes they carry. In Nder and Thiekenne for example, transmission sites were found where both human and cattle contaminate the water (Figure 2) and where B. truncatus and B. globosus occur sympatrically. These snail species have very similar diurnal cercarial shedding patterns, potentially facilitating the infection of single definitive hosts with both parasite species [23],[24]. 10.1371/journal.ppat.1000571.g002 Figure 2 Transmission site in Mbane, Senegal. Hybrid parasites were recovered from snails (Bulinus truncatus) collected at this habitat. Host switching and animal reservoirs The hybridization between S. bovis and S. haematobium is of special interest as S. bovis is a parasite primarily of ruminants and S. haematobium a parasite almost exclusively of man. As our findings were discovered during human parasitological surveys we have, as yet, no data from schistosome infections in local cattle, therefore we cannot speculate on whether S. haematobium or the hybrid can infect cattle. So, in which host is this initial hybridization occurring? A few studies reported S. bovis shaped eggs excreted by man [25]–[27], but it was suggested that this could be due to S. bovis eggs passing through the digestive tract of humans eating infected cow livers. Putative S. haematobium infections have been documented in primates, rodents and artiodactyls [28],[29]. The identification of these infections has relied heavily on egg morphology alone, thus it is possible that hybrids or other morphological similar species were involved. The infectivity of a schistosome to a mammalian host depends on the ability of the cercariae to locate the host, penetrate the skin and evade the host's immune system. The phylogeny of the Schistosoma genus does not show a single origin of human host use suggesting that host switching may have occurred at several time points in schistosome evolution [30]. Phylogenetically, S. haematobium is ancestral to S. bovis [30] and the ability to infect humans may have been retained by S. bovis. Also, as human skin is thinner than the skin of a bovine, it is perhaps more feasible that S. bovis cercariae could penetrate a human rather than S. haematobium managing to infect cows. The exact circumstances facilitating hybridization in either cattle or people need to be determined but immunological factors and co-infections with other pathogens will undoubtedly have a role to play. Another possibility is that the initial pairing between these two schistosome species occurred in a non-human mammalian host that can readily be infected by both species, such as rodents. Rodents are routinely used in laboratories to passage schistosome species, so they are likely to be susceptible in the wild too. However, Duplantier and Sene [31] studied 2000 animals belonging to six different rodent species collected in and around Richard Toll (Senegal) and found only S. mansoni in two rodent species (Arvicanthis niloticus and Mastomys huberti, prevalence of about 5%). Therefore, rodents are unlikely to be involved in this hybridization event, but they might be ideal reservoirs for hybridization between S. mansoni and S. rodhaini [13]. The role of sheep and goats found in the area does also need to be considered. Neglecting the role of animal reservoirs in transmission might contribute to failure of Schistosoma control programmes, as is the case with S. japonicum in Asia that infects humans, livestock, rodents and other animals [32],[33]. At the level of the intermediate snail host, the hybrid increased its host range compared to the parental species. Earlier work has shown that B. truncatus from the Lower and Middle Valley of the SRB is not susceptible to a S. haematobium strain isolated from the Lower Valley, but it is however susceptible to a S. haematobium strain isolated from Mali [34], suggesting a strong role for parasite genetics in this host-parasite relationship. The authors also found that natural transmission of S. haematobium in the Lower Valley is normally associated with B. globosus. In this study we found B. truncatus from Mbane and Rhenne (Lower Valley of the SRB) also to be infected with the hybrid species. It appears therefore that hybridization between S. haematobium and S. bovis is facilitating this breakdown of intermediate snail specificity. This has important implications for the epidemiology of schistosomiasis in northern Senegal because B. truncatus became widespread after dam constructions in the early nineties It seems likely that hybridization may well lead to increased transmission intensities in the Senegal River Basin. Given the small sample size of infected snails in this study, additional screening of cercariae is needed to clarify the exact role of each snail species in parasite transmission. Distribution Our data show that the observed hybridization is not a rare isolated phenomenon, hybrids are being found in human populations located near different tributaries of the SRB, and around Lac de Guiers separated by 5–200 km. In 2004, Sene and colleagues [35] described S. haematobium from Bulinus truncatus collected in Nguidjilone, but our re-inspection of the molecular cox1 data shows that the genetic profiles are in fact identical to the hybrids found in this present study. Nguidjilone is situated in the Middle Valley of the SRB, more than 600 kilometer further east from our study area. Suggestions for natural interactions between S. haematobium and S. bovis were made by Brémond and colleagues [18] who found intermediate egg shapes and intermediate allozyme phenotypes between S. bovis and S. haematobium or S. curassoni collected from children in Niger. Although the allozyme profiles strongly suggested a hybrid origin, the exact role of S. curassoni could not be established as the allozyme markers could not discriminate between S. haematobium and S. curassoni. The authors suggested that S. curassoni could also be involved, through initial hybridization with S. bovis. Indeed hybridization between S. bovis and S. curassoni has been reported in Senegal [36] but this study does not find any proof of S. curassoni involvement. In either case, this and the above data suggest that hybridization between S. haematobium and S. bovis is successful in other areas too and that it has been taking place for some time. This ease of hybridization as suggested by the field data and by the experimental work of Taylor [5], together with the fact that hybrid parasites can infect the very abundant B. truncatus, suggest this interaction may lead to increased transmission in these areas. This, together with the high intensities that can be reached, indicates the need for further screening and experimental studies (see below). Implications Our findings are of utmost importance due to the possible implications that it bears on the disease dynamics and control strategies for these parasites. The acquisition of new genes through introgressive hybridization can lead to phenotypic innovation that can profoundly influence the evolution of disease. Pitchford and Lewis [37] suggested that the poor response of the cattle parasite S. mattheei to oxamniquine treatment might have been due to hybridization with S. haematobium, which is not susceptible to the drug. Hybrids between S. haematobium and S. intercalatum [7],[38] and S. haematobium and S. mattheei [8] acquired an enhanced infectivity to their laboratory hosts, with increased growth rates and reproductive potential. The natural hybridization of S. haematobium and S. guineensis in Cameroon had important consequences on the disease dynamics causing severe disease outbreaks in certain areas [9],[10]. If this new hybrid in Senegal exhibits the same hybrid vigour, it can develop into a new emerging pathogen, necessitating new control strategies in zones where both parental species overlap. Given the increased intermediate host range of the hybrid parasite, an intense and rapid control response is required to minimize further spread of the hybrid and possible escalation of human schistosomiasis. The recent increase in urinary schistosomiasis in the villages along the SRB could be a direct effect of hybrid vigour and/or the use of two abundant snail hosts. The way forward To fully understand the consequences of the introgressive hybridization between these two schistosome species further studies are needed. The recent history of S. haematobium and S. mansoni transmission in northern Senegal is relatively well documented but very little is known about the epidemiology, host use and geographical distribution of S. bovis. A study by Diaw et al. [39] reported a sharp increase in bovine schistosomiasis in the lower valley of the SRB, and the appearance of new infection foci from 1989–1990 onwards. It is important to establish the role of cattle, sheep and other possible mammalian reservoir hosts in these hybridization events through genotyping adult worms and larval stages from these possible reservoirs, and also to determine how each snail species is involved in transmission in these foci. This information together with the screening of other localities will provide further insights into the dynamics and the extent of this hybridization. Experimental infections are needed to study the mating behaviour of S. bovis and S. haematobium and to study the biological characteristics of the hybrid lines such as fecundity, infectivity, longevity, cercarial production and response to praziquantel, the drug used to treat and control schistosomiasis. If it is not as effective in the hybrid, this can result in more pathology and morbidity. Genetic introgression is likely to occur in areas of the genome involved in schistosome biology such as virulence, transmission, host specificity and disease processes. When carefully chosen, microsatellite genotyping can provide a genome-wide view of the level of introgression while direct sequencing of targeted gene regions involved in schistosome biology could provide information for potential drug targets and genes involved in isolating mechanisms, speciation and evolution of the Schistosoma genus. Materials and Methods Ethics statement This study is part of a larger investigation of schistosomiasis epidemiology, transmission and control in Senegal, for which approval was obtained from the ethical committees of the Ministry of Health in Dakar, Senegal, the Institute of Tropical Medicine in Antwerp, Belgium, and the NHS-LREC of Imperial College London, England. According to common practice, all parents and teachers gave oral consent for urine and stool examination and the data were analyzed anonymously. All schistosomiasis positive children were treated with a single dose of praziquantel, at 40 mg/kg of bodyweight. In schools or classes where the percentage of S. haematobium or S. mansoni infections were more than 50%, mass treatment of all children was carried out at the end of the study. Parasite collection Parasitological surveys were carried out in March 2006 and 2007 in six villages within the Senegal River Basin (SRB) separated by about 10 to 150 miles; Tiguet and Gaya along the Senegal River, Mbodjenne on the Lampsar River and Mbane, Thiekenne, Nder on the shores of the Lac de Guier (see Figure 1, 2). To detect the prevalence of urinary and intestinal schistosomiasis, urine and stool samples were taken from 75 school age children per village, with the exception of Nder where 200 children were involved. For S. haematobium detection, 10 mls of each urine sample was filtered using a Nucleopore filter, eggs were viewed and counted under a microscope. Eggs from positive samples were hatched by sedimentation and subsequent exposure to clean water and light. S. mansoni infections were diagnosed by duplicate 41.7 mg Kato Katz for each stool sample. Eggs from positive samples were hatched by homogenising each sample with 0.85% saline solution and then passing it through a metal sieve of 212 µm pore size to remove any larger debris. The remaining aqueous solution containing the eggs was then passed through a home-made Pitchford and Visser funnel [40] and washed copiously with bottled mineral water. The eggs were then concentrated within the Pitchford and Visser funnel and placed in a petri dish where they were exposed to clean water and light. Using a binocular microscope individual miracidia and un-hatched eggs were collected using a Gilson pipette. Where possible egg morphology was recorded by description but no photographs could be taken. S. mansoni eggs have a characteristic lateral spine where as S. bovis and S. haematobium have terminal spines with species specific body shape. Un-hatched eggs were given a further opportunity to hatch by pippetting them into a dish containing fresh water before they were subsequently collected. All samples were individually pipetted onto Whatman FTA® indicator cards in a volume of 3 µl of water and the cards were allowed to dry for 1 hour. Snails caught at the transmission sites were placed into pots containing clean water and exposed to light to stimulate them to shed. Individual cercariae were loaded onto Whatman FTA® indicator cards as described above and the species of snail was identified using morphological characters and recorded. DNA analysis of the FTA samples was carried out at the Natural History Museum in London (Nder material) and the Katholieke Universiteit of Leuven (all other material). FTA DNA extraction A 2.0 mm disc was removed with a Harris Micro Punch from the Whatman FTA® indicator cards at the centre of where the sample was loaded and purified according the manufacturers protocol. Samples were air dried at 56°C for 30 –60 mins. Individual discs were used directly in the multiplex PCR. Primary detection of hybrids This study initially started as routine analysis of S. haematobium and S. mansoni populations using the partial cox1 mtDNA marker with the same PCR primers and conditions as described below. Both the NHM and KUL laboratories involved in the studies discovered unusual cox1 sequences from several eggs and miracidia collected from both urine and stool samples identified as S. bovis. The standard Whatman FTA® indicator cards used in our sampling enable the collection and preservation of large numbers of individual larval schistosome stages under field conditions. However, one drawback is that the FTA punch can only be used once, in a single PCR. Therefore, to detect the hybrids, the nuclear ITS rRNA+cox1 mitochondrial (mt) DNA multiplex PCR was developed for simultaneous amplification of both DNA regions from an individual larval stage (i.e. a single FTA disc). Multiplex PCR and sequencing at the KUL The complete ITS rRNA (981 bp)+partial cox1 mtDNA (585 bp) multiplex PCR amplifications were performed in a total reaction volume of 25 µl and consisted of 1× PCR buffer (Eurogentec), 1.5 mM MgCl2 (Eurogentec), 200 µM of each dNTP (Amersham Pharmacia Biotech, Sweden), 1 µM of each primer (Eurogentec; Asmit1 TTTTTTGGTCATCCTGAGGTGTAT [41] and Schisto 3′ TAATGCATMGGAAA-AAAACA [42], ITS4: TCCTCCGCTTATTGATATGC and ITS5: GGAAGTAAAAGTCGTAACAAG [43], 1 unit Taq polymerase (Eurogentec), milli-Q water and the individual purified FTA disc. PCR parameters were 3 min at 96°C followed by 40 cycles of 30 sec at 95°C, 30 sec at 54°C and 1 min at 72°C, followed by a final cycle at 72°C for 7 min. The PCR products were visualized on a 1.5% ethidium bromide agarose gel, gel extracted and purified by means of GFX columns according to the manufacturer's instructions (Amersham Pharmacia). The purified products were sequenced using a Big Dye Chemistry Cycle Sequencing Kit (version 1.1) in a 3130 DNA Analyzer (Applied Biosystems), using the original PCR primers. Multiplex PCR and sequencing at NHM The complete ITS rRNA (981 bp)+partial cox1 mtDNA (585 bp) multiplex PCR amplifications were performed in a total reaction volume of 25 µl using Ready-to-go PCR Beads (Amersham Pharmacia Biotech) each containing 1.5units DNA Taq Polymerase, 10 mM Tris-HCl (pH 9), 50 mM KCl, 1.5 mM MgCl2, 200 µM of each dNTP and stabilizers including BSA, 10 pmol of each primer (cox1 primers as above) and ITS primers - ITSF: TAACAAGGTTTCCGTAGGTGAA, ITSR: TGCTTAAGTTCAGCGGGT [44] and the individual purified FTA disc. Thermal cycling was performed in a Perkin Elmer 9600 Thermal Cycler and the PCR conditions used were: 5 min denaturing at 95°C: 40 cycles of 30 sec at 95°C, 30 sec at 40°C, 1 min at 72°C; followed by final extension period of 7 min at 72°C. 25 µl of each amplicon were run out on 1.5% Ethidium bromide agarose gel until good separation of the ITS and cox1 bands could be seen using the UVP system. Each ITS and cox1 band was gel extracted and purified using Qiagen PCR gel extraction Kits (Qiagen) according to the manufacturer's protocol. Each band was sequenced with the original PCR primers using a Fluorescent Dye Terminator Sequencing Kit (Applied Biosystems) and the sequencing reactions were run on an Applied Biosystems 377 automated sequencer. The sequences were assembled and manually edited using Sequencher ver 4.5 (GeneCodes Corp.). Identity of the sequence was confirmed using the Basic Local Alignment Search Tool (BLAST) and by comparison with reference alignments. At the polymorphic positions of the ITS between S. haematobium and S. bovis any occurrence of double chromatogram peaks was recorded to identify mixed ITS sequences. Sequences are submitted to Genbank under Ac. Nos. FJ588850-62. Reference samples/Controls (NHM) Genomic DNA from schistosomes from Senegal stored in the NHM liquid nitrogen collection was extracted using the DNeasy extraction kit (Qiagen). S. haematobium from Guede Chantier, S. mansoni from Richard Toll, S. bovis from St. Louis and S. curassoni from Guede Chantier were used. S. curassoni was included to rule out any possible involvement in our findings. The cox1 and ITS sequences were amplified from the reference samples as described above and these sequences were used as templates to identify and compare the samples in this study. The pair-wise uncorrected distances between the cox1 sequences were calculated using MEGA 4.1 [45].
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                Author and article information

                Journal
                Proc Natl Acad Sci U S A
                Proc. Natl. Acad. Sci. U.S.A
                pnas
                pnas
                PNAS
                Proceedings of the National Academy of Sciences of the United States of America
                National Academy of Sciences
                0027-8424
                1091-6490
                12 November 2019
                28 October 2019
                28 October 2019
                : 116
                : 46
                : 23182-23191
                Affiliations
                [1] aSchool of Aquatic and Fishery Sciences, University of Washington , Seattle, WA 98195;
                [2] bHopkins Marine Station, Stanford University , Pacific Grove, CA 93950;
                [3] cWestern Ecological Research Center, United States Geological Survey , Santa Barbara, CA 93106;
                [4] dMarine Science Institute, University of California, Santa Barbara , CA 93106;
                [5] eAquatic and Terrestrial Ecology, Royal Belgian Institute of Natural Sciences , 1000 Brussels, Belgium;
                [6] fDepartment of Biological Sciences, Virginia Polytechnic Institute and State University , Blacksburg, VA 24060;
                [7] gDepartment of Biology and Marine Biology, University of North Carolina Wilmington , Wilmington, NC 28403;
                [8] hEmmett Interdisciplinary Program in Environment and Resources, Stanford University , Stanford, CA 94305;
                [9] iDepartment of Ecology and Evolutionary Biology, University of California, Los Angeles , CA 90095;
                [10] jDepartment of Biological Sciences, Environmental Change Initiative, Eck Institute of Global Health, University of Notre Dame , Notre Dame, IN 46556;
                [11] kWolfson Wellcome Biomedical Laboratories, Department of Life Sciences, Natural History Museum , London SW7 5BD, United Kingdom;
                [12] lLondon Centre for Neglected Tropical Disease Research, Imperial College London School of Public Health , London W2 1PG, United Kingdom;
                [13] mCentre for Emerging, Endemic, and Exotic Diseases, Department of Pathology and Population Sciences, Royal Veterinary College, University of London , London NW1 0TU, United Kingdom;
                [14] nBiomedical Research Center Espoir Pour La Santé , BP 226 Saint-Louis, Senegal;
                [15] oStation d’Innovation Aquacole , BP 524 Saint-Louis, Senegal
                Author notes
                1To whom correspondence may be addressed. Email: chelwood@ 123456uw.edu .

                Edited by Clément Lagrue, University of Otago, Dunedin, New Zealand, and accepted by Editorial Board Member David W. Schindler September 18, 2019 (received for review March 13, 2019)

                Author contributions: C.L.W., S.H.S., I.J.J., A.J.C., K.D.L., A.M.K., M.J., S.H., F.A., B.W., M.R., J.P.W., S.S., N.J., G.R., and G.A.D.L. designed research; C.L.W., S.H.S., I.J.J., A.J.C., M.J., S.H., J.C.B., A.J.L., A.E.G.-V., F.A., B.W., M.R., J.P.W., L.B., R.N., S.S., N.J., and G.A.D.L. performed research; C.L.W., S.H.S., I.J.J., S.H., G.A., F.A., B.W., M.R., J.P.W., and G.A.D.L. contributed new reagents/analytic tools; C.L.W., S.H.S., I.J.J., S.H., G.A., E.F., and G.A.D.L. analyzed data; and C.L.W., S.H.S., I.J.J., A.J.C., K.D.L., A.M.K., M.J., S.H., G.A., J.C.B., A.J.L., A.E.G.-V., E.F., J.R.R., F.A., B.W., M.R., J.P.W., L.B., R.N., S.S., A.-M.S., N.J., G.R., and G.A.D.L. wrote the paper.

                Author information
                http://orcid.org/0000-0003-2738-3139
                http://orcid.org/0000-0002-5421-0148
                http://orcid.org/0000-0002-7946-5876
                http://orcid.org/0000-0002-4186-3369
                Article
                201903698
                10.1073/pnas.1903698116
                6859407
                31659025
                b0887c49-e77d-447c-85ed-9931b226a327
                Copyright © 2019 the Author(s). Published by PNAS.

                This open access article is distributed under Creative Commons Attribution License 4.0 (CC BY).

                History
                Page count
                Pages: 10
                Funding
                Funded by: Michigan Society of Fellows at the University of Michigan
                Award ID: NA
                Award Recipient : Chelsea L Wood Award Recipient : Susanne H. Sokolow Award Recipient : Isabel Jones Award Recipient : Andrew J Chamberlin Award Recipient : Merlijn Jocque Award Recipient : Andrea Lund Award Recipient : Giulio A. De Leo
                Funded by: Alfred P. Sloan Foundation 100000879
                Award ID: Sloan Research Fellowship
                Award Recipient : Chelsea L Wood
                Funded by: Wellcome 100010269
                Award ID: SCAN Project WT104958MA
                Award Recipient : Fiona Allan Award Recipient : Muriel Rabone
                Funded by: Bill and Melinda Gates Foundation (Bill & Melinda Gates Foundation) 100000865
                Award ID: OPP1114050
                Award Recipient : Susanne H. Sokolow Award Recipient : Isabel Jones Award Recipient : Andrew J Chamberlin Award Recipient : Merlijn Jocque Award Recipient : Andrea Lund Award Recipient : Giulio A. De Leo
                Funded by: Stanford University Woods Institute for the Environment
                Award ID: Environmental Venture Program
                Award Recipient : Chelsea L Wood Award Recipient : Susanne H. Sokolow Award Recipient : Isabel Jones Award Recipient : Andrew J Chamberlin Award Recipient : Merlijn Jocque Award Recipient : Andrea Lund Award Recipient : Giulio A. De Leo
                Funded by: Stanford University Freeman Spogli Institute
                Award ID: GDP SEED grant
                Award Recipient : Chelsea L Wood Award Recipient : Susanne H. Sokolow Award Recipient : Isabel Jones Award Recipient : Andrew J Chamberlin Award Recipient : Merlijn Jocque Award Recipient : Andrea Lund Award Recipient : Giulio A. De Leo
                Funded by: HHS | National Institutes of Health (NIH) 100000002
                Award ID: R01TW010286
                Award Recipient : Susanne H. Sokolow Award Recipient : Isabel Jones Award Recipient : Andrew J Chamberlin Award Recipient : Merlijn Jocque Award Recipient : Andrea Lund Award Recipient : Giulio A. De Leo
                Funded by: National Science Foundation (NSF) 100000001
                Award ID: 1414102
                Award Recipient : Susanne H. Sokolow Award Recipient : Isabel Jones Award Recipient : Andrew J Chamberlin Award Recipient : Merlijn Jocque Award Recipient : Andrea Lund Award Recipient : Giulio A. De Leo
                Categories
                PNAS Plus
                Biological Sciences
                Ecology
                PNAS Plus

                bilharzia,ecological levers for infectious disease control,snail control,spatial ecology,urogenital schistosomiasis

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