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Population genomic analyses of schistosome parasites highlight critical challenges facing endgame elimination efforts

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Scientific Reports
Authors:
  • NOAA Alaska Fisheries Science Center
  • University of North Texas Health Science Center

Abstract and Figures

Schistosomiasis persists in Asian regions despite aggressive elimination measures. To identify factors enabling continued parasite transmission, we performed reduced representation genome sequencing on Schistosoma japonicum miracidia collected across multiple years from transmission hotspots in Sichuan, China. We discovered strong geographic structure, suggesting that local, rather than imported, reservoirs are key sources of persistent infections in the region. At the village level, parasites collected after referral for praziquantel treatment are closely related to local pre-treatment populations. Schistosomes within villages are also highly related, suggesting that only a few parasites from a limited number of hosts drive re-infection. The close familial relationships among miracidia from different human hosts also implicate short transmission routes among humans. At the individual host level, genetic evidence indicates that multiple humans retained infections following referral for treatment. Our findings suggest that end-game schistosomiasis control measures should focus on completely extirpating local parasite reservoirs and confirming successful treatment of infected human hosts.
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
Scientic Reports | (2021) 11:6884 | 
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Population genomic analyses
of schistosome parasites highlight
critical challenges facing endgame
elimination eorts
Jonathan A. Shortt1,2,7, Laura E. Timm1,7, Nicole R. Hales3, Zachary L. Nikolakis3,
Drew R. Schield3,4, Blair W. Perry3, Yang Liu5, Bo Zhong5, Todd A. Castoe3,7,
Elizabeth J. Carlton6,7 & David D. Pollock1,7*
Schistosomiasis persists in Asian regions despite aggressive elimination measures. To identify
factors enabling continued parasite transmission, we performed reduced representation genome
sequencing on Schistosoma japonicum miracidia collected across multiple years from transmission
hotspots in Sichuan, China. We discovered strong geographic structure, suggesting that local, rather
than imported, reservoirs are key sources of persistent infections in the region. At the village level,
parasites collected after referral for praziquantel treatment are closely related to local pre-treatment
populations. Schistosomes within villages are also highly related, suggesting that only a few parasites
from a limited number of hosts drive re-infection. The close familial relationships among miracidia
from dierent human hosts also implicate short transmission routes among humans. At the individual
host level, genetic evidence indicates that multiple humans retained infections following referral
for treatment. Our ndings suggest that end-game schistosomiasis control measures should focus
on completely extirpating local parasite reservoirs and conrming successful treatment of infected
human hosts.
Schistosomiasis is a neglected tropical disease that impacts an estimated 200 million people globally13 causing
brosis of the liver and bladder, anemia, and in some species, cancer1,2,4,5. Schistosomiasis control programs in
China, beginning in the 1950s, are responsible for a 99% reduction in schistosomiasis infection prevalence, with
approximately 54,000 infections in China in 201668. e modern schistosomiasis control program in China is a
multi-pronged strategy including health education, testing and treatment, application of molluscicides to snail
habitat, and treatment of bovines9,10. While control programs are generally eective9,10, transmission hotspots
remain for reasons that are not well understood11,12. Several regions, including regions outside of China13, have
experienced re-emergence of schistosomiasis or no further declines in prevalence11, and our team, among oth-
ers, has found high infection rates in recent years14. ese infections are perplexing partly because they arise in
areas where control programs are ongoing and infected snails are not readily identied10.
e persistence of infection despite ongoing control measures highlights gaps in our knowledge of the natural
history of schistosomes and the epidemiology of schistosome infection. As China continues towards the goal of
schistosomiasis elimination by 202515, new insights into factors aecting schistosome transmission are needed.
Evolutionary and population genetic studies can yield insights that can be used to ll these gaps and increase
the eectiveness of control programs, such as how parasite populations change in response to mass administra-
tion of chemotherapy16. An in-depth understanding of S. japonicum population structure in Sichuan, China—a
region currently experiencing schistosomiasis re-emergence despite on-going, aggressive control measures10—can
OPEN
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provide crucial and actionable insights into how a parasite population on the brink of elimination is able to
persist.
Detailed insight into schistosome transmission patterns in response to treatment could inform future control
programs implemented in other parts of the world where parasitic helminths are endemic. Most population
genetic studies in schistosomes have been limited by the number of loci, small sample sizes, or both1721, and
thus provided limited resolution in answering questions about population structure. However, recent advances
in genomic technologies are making it possible to address previously inaccessible questions and promise to grant
greater insight into the persistence of schistosome infections. Here, we apply a reduced representation genome
sequencing approach2224 to sample tens of thousands of single nucleotide polymorphisms (SNPs) from hun-
dreds of miracidia (the ospring of infective schistosome mating pairs) longitudinally collected across nearly a
decade. ese data provide unprecedented resolution of patterns of schistosome population structure across a
geographically small area in Sichuan, China that highlight key features of regional infection hotspots. We further
describe an approach to discern between dierent degrees of relatedness, enabling the inference of source infec-
tions using high-resolution genomic data.
Results
In total, 272 miracidia preserved on FTA indicator cards were sequenced using double digest restriction-site asso-
ciated DNA sequencing (ddRADseq)25. is reduced representation genome sequencing approach was applied
following whole genome amplication, and generated a total of 1.8B reads. Aer ltering sequences for quality,
mapping reads to the S. japonicum reference genome, and excluding both low-coverage loci (Supplementary
Fig.S1) and miracidia with excess missing genotypes, there were 72,797 variable sites in 200 miracidia. e
details of the distribution of these miracidia across hosts and villages are provided in Supplementary TableS1. We
further ltered out low-condence SNP calls as missing data, resulting in a nal set containing 33,901 variants.
Population analyses. To determine whether schistosome infections are acquired from local or regional
sources, we evaluated the spatial distribution of schistosome genetic diversity across the study region. Genetic
structure indicates that the parasites are more related within villages than between villages, with allele sharing
decreasing signicantly with geographic distance between villages (Fig.1a,b, Supplementary Fig.S2). Population
structure is strong enough that most villages have a unique, discernible population of miracidia. For example,
the rst two principal components in principal component analysis (PCA) of genetic variation across samples
distinguish miracidia in the two most distant villages, C (the northernmost village sampled in this study) and D
(the southernmost village), from other villages (Fig.1c); additional principal components separate most other
villages into clear clusters based on genetic similarity (Supplementary Fig.S3). Phylogenetic analysis of mira-
Figure1. Genetic and geographic structure of Schistosoma japonicum miracidia sampled in Sichuan, China.
(a) Map showing locations of the 12 villages sampled, indicated by colored dots. Yellow lines represent major
roads and blue lines indicate rivers and major streams. e map was created with ArcGIS ArcMap52 (version
10.6; https:// deskt op. arcgis. com/ en/ arcmap/). (b) Proportion of rare alleles shared among villages with mean,
interquartile ranges, and outliers beyond the 2.5th percentile shown. Inter-village distances are Euclidean. All
comparisons were signicantly dierent (all p < 2.2 × 10–16; Mann–Whitney U test). (c) Principal component
analysis (PCA) of genetic variation from 200 miracidia across all 12 villages. e rst two principal components
(PC1 and PC2) respectively account for 4.2% and 2.5% of the genetic variation among individuals. (d)
Neighbor-joining tree of miracidia colored by village (top) and sampling timepoint (bottom). (e) ADMIXTURE
plot showing optimal k = 4 genetic clusters grouped by village and sampling timepoint. Timepoints are labeled
with year of collection (e.g., 2008 in d or 08 in e); Summer and late Fall 2016 collections are labeled with small s
or f, respectively.
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cidia also clusters villages, with most villages occupying their own clade (Fig.1d, Supplementary Fig.S4). is
trend was not seen when neighbor-joining trees were labeled by timepoint (Fig.1d). Estimates of population
structure using ADMIXTURE26 support this nding and identify further substructure within villages, particu-
larly village C (Fig.1e).
e genetic structure of schistosomes within villages indicates that local infection sources were not fully
eliminated by whole-village praziquantel treatments between sampling points. Miracidia from the same village
fall into characteristic ADMIXTURE clusters regardless of sampling timepoint (Fig.1e, villages A, B, C, E, and H;
see also Supplementary Figs.S4, S5), and miracidia collected from the same timepoint fall into multiple clades
on the phylogenetic tree (Fig.1d). However, there is a notable dierence in genetic structure in village J (within
the eastern cluster of villages) between 2010 and 2016, the largest time span present in the data (Fig.1d,e). While
structure appears to be retained over time in many cases, our ability to conduct longitudinal sampling for every
village was limited and the extent to which population structure is conserved is variable. Our resolution is also
limited by limited sampling of hosts in particular villages, with some villages represented by a single individual
host.
To conrm that broad patterns in our results were robust when sibling miracidia were removed, a sibling-
pruned dataset was generated and analyzed in the same way as the full dataset. Results of these analyses were
indeed qualitatively similar to those based on the full dataset and are presented in Supplementary Figs.S6–S10.
Identication of family clusters and relatedness estimates. Measures of relatedness among mira-
cidia allow inference of ne-scale transmission patterns. In the absence of reliable allele frequencies and/or
robust linkage information, we used the proportion of rare alleles shared between all pairs of miracidia to cal-
culate the posterior probabilities of rst-, second-, third-, or fourth-degree relationships between members of a
pair (Fig.2a; Supplementary TableS2). We nd evidence that miracidia from the same village tend to be closely
related (Figs.1b and 2b). Posterior probabilities of relatedness calculated from allele sharing (“Methods”) indi-
cate that schistosome rst cousins (3rd degree relatives) are extremely common within villages, but much rarer
between villages (Fig.2b). Because we only sample the progeny of adult mating schistosomes, a rst-degree
relationship between a pair of miracidia indicates that members of the pair are siblings, and as expected, pairs
of miracidia collected from the same human host are oen siblings (1st degree relatives; Fig.2b). However, we
also nd a large number of 2nd degree relatives within villages (Fig.2c, village D). It seems reasonable that most
of these are double rst cousins, given the high frequency of rst cousins within villages. Separate clutches of
parasite siblings were identied within individual human hosts (Fig.3a), indicating infection by multiple mating
pairs. We also found multiple examples of human hosts with sibling clusters that span multiple sampling time-
points (Fig.3b); while the possibility that a human host was reinfected with clones cannot be discounted, this is
preliminary evidence of retained infection despite the host being referred for intervening treatment protocols
(Fig.3b). One instance of a cross-timepoint sibling cluster was sampled in 2016, when the region implemented
directly observed treatment (DOT). Infections detected prior to 2016 could have, in principle, been retained
due to non-compliance with treatment. However, the retained infection detected aer DOT raises questions
about the eectiveness of treatment protocols and concerns that human hosts who failed to clear their infections
despite drug treatment may have served as sources of new infections to other community members.
High levels of allele sharing within villages (Fig.3c) indicate that parasite mate choice is oen limited to rela-
tives during the reinfection process. is limitation implies that following treatment, infections in a village may
have been re-established by a small number of genetically unique schistosomes, likely reecting the eectiveness
of local schistosomiasis control programs10,27. However, these results also suggest that long-term elimination
may require identication and targeted treatment of remaining local parasite sources. e genetic structure of
schistosomes within villages indicates that local infection sources were not fully eliminated by whole-village
praziquantel treatments between sampling points. For example, we inferred two possible treatment failures based
on the identication of apparent siblings collected from the same host before and aer treatment cycles, one of
which was sampled at two timepoints in 2016, when treatment was directly observed (Fig.3b).
e existence of clones could produce false inferences of sibling relationships (and thus retained infections)
within individual hosts across timepoints, and cannot be ruled out entirely if the number of cercaria-emitting
snails in the environment is small enough that individuals are reinfected with identical worms from the same
snails, or if identical juvenile worms residing in the liver survive treatment. We discount this partly due to the
~ 6-month lifespan of infected Oncomelania snails28 and the months required to develop worms from cercariae
and form mating pairs within a human host. Time-separated clonal double infections would require the envi-
ronmental condition that the individual snails produce clonal cercariae from the time of the initial infection
(followed by development, mate pairing, detection, and treatment—a minimum of 40 days29) until the time of the
second infection. In contrast, the retention of infections over time, due either to non-compliance with treatment
or treatment failure, is a more obvious explanation and supported by prior evidence14. Furthermore, cross-host
siblings indicating clonal pairs are rare (Fig.3c). us, we generally expect that clonality has had little impact on
our within-host inferences of retained infection. Instead, the detection of schistosome clones between human
hosts suggests that schistosomiasis control eorts have been highly eective in reducing local snail populations
required for producing cercariae.
Discussion
Our results highlight the important role of epidemiological and genomic data to resolve transmission patterns in
areas approaching elimination. ree major trends apparently contributed to the persistence of schistosomiasis
in the residual transmission hotspots we studied. First, local parasite reservoirs were a major contributor to
local re-introduction of schistosome infections. is is demonstrated by the nding that village miracidia are
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Figure2. Genetic relatedness of Schistosoma japonicum miracidia within and between villages. (a) Heatmap of allele sharing between all
sampled Schistosoma japonicum miracidia. Rows and columns are ordered using hierarchical clustering and annotated with village and
timepoint. (b) Distributions are shown for allele sharing between miracidium pairs sampled from dierent villages (blue), within villages
but dierent hosts (grey), and within hosts (green). e posterior probabilities for dierent degrees of relatedness are indicated by width
for 1st to 4th degree relatives in the lower plot. (c) Distributions of within-village (top panel) and within-host (lower panel) allele sharing
are shown for villages C (green) and D (orange). e total number of comparisons underlying each distribution is shown on the right.
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comprised of closely related populations of S. japonicum across timepoints, despite prompt referral for treatment
of all positive infections and complementary eorts to eliminate schistosomiasis from these villages during the
study period. Second, there is apparent retention of infection in individual hosts despite referral for treatment.
Strong evidence for this is provided by identication of sibling clusters from the same human host during
sampling events separated by seasons or years. ird, the high degree of relatedness of miracidia from dierent
hosts suggests that humans likely participate in maintaining local schistosomiasis reservoirs and amplify local
transmission events, although the participation of non-human mammals cannot be excluded.
We nd clear evidence for the successful impact of control measures on population dynamics in S. japonicum.
is result is somewhat dierent from some studies in S. mansoni and S. haematobium/S. bovis that observed
high gene ow among neighboring populations3032. It seems reasonable to suppose that the dierence may lie in
the long-term, focused, and comprehensive nature of Chinese schistosome control eorts (which have induced
extremely low observed snail abundance), as well as the rural, mountainous topography of our study region. We
note that it is not possible to draw denitive conclusions about village-wide population structure in ve villages
where miracidia were collected from a single host (Supplementary TableS1), however based on the observation
Figure3. Relatedness of Schistosoma japonicum miracidia within and between hosts. Examples highlight
relatedness structures indicating multiple infections, retained infections, evidence for clones, and inbreeding
within villages. Hosts are indicated with human gures, with dierent miracidia collected from a single
host connected by thin dark grey lines. Ribbons between miracidia show posterior probabilities of degree of
relatedness through color (scale to side) and by ribbon width. (a) Two examples of multiple sibling clusters (2
and 4) within hosts are shown. In the second example, 8 miracidia are not in sibling clusters (all connections are
in light grey), indicating a high multiplicity of infection sources (a minimum of 12 mating pairs) in this host. (b)
Two examples of likely retained infections over time are inferred from the sibling-level miracidia sampled from
the same host at dierent timepoints separated by ve months and two years. (c) Miracidia from multiple hosts
living in villages B, J, and D and sampled at the same timepoint are shown with gaps between dierent villages.
In the le graph, sibling-level relatedness is shown, and a case of sibling-level relatedness between miracidia
across two individuals indicates clonal parents. In the right graph, cousin-level relatedness emphasizes that
strongly supported rst-cousin relationships are common among miracidia within villages and sparse between
villages.
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that population structure in the more densely-sampled villages is generally stronger between villages than within
villages, it seems reasonable to expect that denser sampling within these villages would reveal similar patterns.
Evidence of retained individual infections across sampled timepoints in our local study system raises ques-
tions about the negative impact of occasional treatment failures on the eectiveness of control measures. Spe-
cically, human hosts who fail to clear their infections may serve as sources of new infections to other humans.
e extent to which human vs. non-human mammalian hosts serve as sources of new infections is an extremely
important factor for guiding control eorts. If human hosts sometimes fail to clear their infections following
treatment and subsequently serve as sources of infection to others, the eectiveness of treatment protocols
should be reviewed and improved. We caution that the frequency and causes of retained infection remain
uncertain—including the extent to which treatment failure is due to drug resistance33, suboptimal dosing34, or
non-compliance with treatment35—and warrant further investigation. Furthermore, S. japonicum is a zoonosis
and it is dicult to eliminate non-human mammalian hosts as local reservoirs and ampliers of human infec-
tions. Now that the importance of local reservoirs has been established, ongoing sampling eorts will include a
variety of such alternate hosts.
Furthermore, the evidence for inbreeding among schistosomes complicates the evaluation of short inter-
human infection pathways. Such evaluation is also complicated because the human-infective cercaria stage
of schistosomes that originates from snails is clonal, and genetically identical cercariae may produce multiple
infections in one or more human hosts36. e most direct human-to-human infection pathway, involving only a
snail intermediate host, would yield avuncular relationships between miracidia from each host (Fig.4). However,
because of inbreeding and clonality, we were unable to dierentiate between the types of 2nd degree relations
(double rst cousins, half-siblings, or avuncular). Due to the high frequency of rst-cousin level relationships
within villages, we suspect that many, if not most, of the 2nd degree relations observed are double rst cousins.
Although rare, observations of sibling-level relatives across human hosts demonstrate that clonal infections
occurred in our samples (Fig.3c), and so clonal infections could also explain some 1st and 2nd degree relatives
observed between human hosts.
We expect that some of these questions can be resolved by the sampling and acquisition of denser variant
information with more loci per Mbp. Increased directed sampling will enable the estimation of key epidemio-
logical parameters such as the frequency of treatment failure, the number of active mating pairs within a human
host, and the frequency of clonal infections. Sampling of non-human mammalian hosts can potentially establish
a role for such hosts as both reservoirs and ampliers of re-introduced human infections. It is worth noting that
it may not be possible to eliminate a role for non-human hosts. If non-human hosts contribute low-frequency
infection rates or if a non-human host type is unidentied, such sources become nearly impossible to detect.
Denser variant information, such as that obtained by whole genome sequencing, along with recent improvements
in the S. japonicum reference genome37, will allow construction of extended haplotypes (local linkage groups)
that should be able to better distinguish among types of 2nd degree relatives and potentially extend pedigrees.
Such denitive inference of infection pathways would allow the establishment of frequencies of transmission
routes in the local schistosome re-establishment.
e work presented here exemplies how population genomic studies can illuminate factors underlying
transmission of macroparasites and provide strategic and precise advice to direct control eorts. We nd that
there are high levels of schistosome inbreeding within villages, that there are consistent, local sources of infection
through time, and that some human hosts appear to retain infections despite treatment referral. ese ndings
indicate that the persistence of schistosomiasis in residual transmission hotspots is primarily driven by local
transmission and reinfection, with at least some contribution from humans. Based on our ndings, end-game
Figure4. Avuncular relationships among schistosome miracidia. Diamonds indicate schistosomes, with those
surrounded by a gray box indicating an adult mating pair, and those surrounded by a dashed box indicating
miracidia sibling clutches. Chromosomes within diamonds are colored to indicate dierent haplotype
combinations that could be inherited from parents. e arrow points to a sibling of a miracidia clutch collected
from Host 1 that became a parent of another sibling clutch collected from Host 2. is worm is the link that
creates the depicted avuncular relationship between the ospring of schistosomes within Host 1 and Host 2.
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control measures should focus on conrmation of schistosome elimination from infected human hosts and
complete extirpation of local infection reservoirs.
Materials and methods
Miracidia collection and sample selection. Miracidia, the rst schistosome larval stage, were collected
from 12 villages in Sichuan, China (see Fig.1a). Infection surveys took place in 2007, 2008, 2010, and in both
the summer and fall of 2016. During each survey, village residents submitted fecal samples for three consecutive
days and each sample was tested for S. japonicum infection using the miracidium hatching test as described in
the literature23. Individual miracidia were collected from the top of the hatching test ask, rinsed three times
in autoclaved, de-ionized water and transferred to Whatman FTA indicator cards using a hematocrit tube or
Pasteur pipette drawn to a narrow bore with a ame.
A subset of collected samples were selected for inclusion in the study. is subsampling was designed to
include 10–15 miracidia from every village and across multiple timepoints. When possible, we tried to include
multiple samples from the same human host and multiple human hosts from each village. However, ve villages
(E, F, I, K, and L) presented here are represented by multiple miracidia collected from a single host (Supple-
mentary TableS1).
e research involving human subjects was approved by the Sichuan Institutional Review Board, the Uni-
versity of California, Berkeley, Committee for the Protection of Human Subjects, and the Colorado Multiple
Institutional Review Board. Participants provided written, informed consent. All experiments were performed
in accordance with relevant guidelines and regulations. Anyone testing positive for Schistosoma japonicum was
informed of their infection status and referred to the local anti-schistosomiasis control station for treatment.
DNA library preparation and sequencing. DNA library preparation followed a previously published
methodology24. Briey, discs containing individual miracidia were excised from Whatman FTA cards using a
2mm card punch (Whatman WB100029) and DNA from the disc was whole-genome-amplied by isothermal
genome amplication, termed “multiple displacement amplication” (MDA), using GenomiPhi v3 (GE Health-
care Biosciences 25660124) amplication tubes with modications as described in the literature24. Amplied
DNA was digested for > 8h with PstI-HF and Sau3AI at 37°C followed by a 65°C heat deactivation step. Fol-
lowing solid phase reverse immobilization (SPRI) DNA extraction, custom adaptors containing an 8-bp unique
molecular identier (UMI) and sequences corresponding to the single-stranded DNA sticky ends generated by
digestion and a 6-bp barcode were ligated to digested fragments. Adaptors ligating to PstI-HF cuts also contained
6-bp barcodes. Following ligation, sets of 6–8 samples were pooled such that no barcode was used twice within
the same pool, and underwent size selection for fragments sizes either 300–600bp (including adaptor sizes) or
390–690bp (including adaptor sizes) using a PippinPrep with a 1.5% agarose gel. Following size selection, sam-
ples underwent 15 cycles of PCR amplication. Primers used in amplication also contained index sequences
and sequences used for Illumina-based sequencing cluster formation (sequences for all adaptors and primers are
shown in Supplementary TableS3). Sample pools were then combined in equimolar ratios such that no index
sequence was used more than once within each pool. Samples were sequenced on an Illumina HiSeq using v4
chemistry.
Fastq processing and variant identication. In total, 272 samples were sequenced: 124 samples with
125-bp single end reads each, and 148 samples with 150-bp paired end reads each, resulting in 1,799,089,548
total reads generated. PCR clones were ltered from the reads with the clone lter tool in stacks38 using the
UMIs contained in each barcode. Sequences were then quality ltered and divided by barcode using the pro-
cess_radtags tool in stacks38 with restriction enzymes and barcodes supplied as arguments. We ‘rescued’ reads
with a single base mutation in the 8-bp barcode or restriction sites (-r). Low-quality reads were removed (-q) to
a separate le (-D) and excluded from downstream analysis. On average, 5.61% of reads from each library were
identied as clones and removed. An average of 31.37% of reads were ltered from each library due to clonality,
ambiguous barcodes/restriction site, or quality, though one library containing barcoded DNA from eight mira-
cidia contained an abnormally high number of reads missing restriction sites in the correct place. is library
was retained, with the lters above applied. Excepting this library, an average of 26.96% of total reads were
ltered from all reads. Reads passing this series of lters were mapped to the S. japonicum reference genome
(downloaded from schistodb.net39,40) using bwa mem41. Variants were called from .bam les using Haplotype
Caller in the Genome Analysis Toolkit4244 with gvcf mode and GenotypeGVCFs. Over 4 million variant sites
were found, however most of these sites were sequenced in just one or very few miracidia. Demultiplexed fastq
les, as well as bam and bam index les, are available through the NCBI Sequence Read Archive (SRA) database
under BioProject PRJNA349754.
Dening sets of ddRADseq loci. Although most ddRADseq reads mapped reliably to expected ddRAD-
seq loci24, loci from o-target reads may add noise to subsequent analyses. To de-noise our data, we identied
a set of loci that were reliably recovered at 20 × depth across the majority of samples in order to retain only
those variants that map to ddRADseq loci. Using a custom perl script (cutgenome.pl; github.com/PollockLabora-
tory/Schisto), we identied the expected mapping locations of ddRADseq reads in the S. japonicum reference
genome40, with each expected individual ddRADseq locus having two dierent locations: one for the forward
read and one for the reverse read, if applicable.
To identify the subset of these expected loci that could be reliably recovered, we rst eliminated miracidia
that had fewer than 500K reads post-ltering or less than 20K reads that map to the reference genome with a
mapq ≥ 20. We obtained the sequencing depth of each expected ddRADseq locus in each of these 156 remaining
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‘high-depth’ miracidia using bedtools45 intersect. We recorded the coverage of each expected read locus (-c) and
required that mapped loci overlapped by at least 50% of an expected read length before incrementing the depth
count (-f 0.5). For miracidia that were sequenced with single end sequencing, the cumulative depth of each of the
fragment’s possible reads was used as the depth for the locus; for miracidia sequenced with paired end sequenc-
ing, the mean depth of the two read loci was used for the fragment’s depth.
From this data set, we identied 9637 expected ddRADseq loci sequenced at 20 × depth in 75% of ‘high-
depth’ miracidia (see Supplementary Fig.S1). To further restrict variants to the most stringent loci, analyses
reported here used only variants from the 6990 expected ddRADseq loci that were close to the target size selection
range (170–500bp). Once these high-condence loci were identied, they were called across the entire dataset,
resulting in reads across 200 samples.
Variant set creation. Variants then underwent a number of lters as follows: invariant sites were removed,
sites with more than two alleles or that contained an indel were removed, and variants that were not within
an expected ddRADseq locus were removed. To create our nal variant set, we re-coded any sites sequenced
at < 10 × coverage as missing data, recoded individual genotypes with GQ < 20 as missing, removed sites that
were missing more than 50% of genotype calls, and removed miracidia missing more than 90% of genotype calls
(Supplementary Fig.S11). is nal ltering resulted in 200 miracidia genotyped at 33,901 sites. e .bed le
and .vcfs from dierent stages of ltering can be downloaded from http:// www. Evolu tiona ryGen omics. com/
Progr amsDa ta/ Schis toGen omics.
Population analyses. e parametric tests for population structure we performed require that the pro-
vided loci be in linkage equilibrium, however missing genetic distances between neighboring sites and the cur-
rently highly fragmented reference genome makes linkage pruning dicult. is problem is compounded in
our dataset because a large proportion of the miracidia were suspected to be highly related, which could inate
linkage estimates between sites. Here, we outline the steps we performed to obtain a set of variants likely to be
unlinked (though we note that this pruning does not guarantee that all sites used are in linkage equilibrium).
We rst identied miracidia that are expected to be closely related by identifying clusters of miracidia that
share a proportion of rare alleles greater than 0.45 (see “Identication of family clusters and relatedness esti-
mates” below) between each pair of miracidia, and removed all but one miracidium from each cluster. A total of
83 miracidia remained following this step (see “Identication of family clusters and relatedness estimates” for
details). We then pruned linked variants in this putative unrelated set using plink’s –indep-pairwise command
(v1.90b4.6)46 with arguments 1000 100 0.1, which greedily prunes variants with r2 > 0.1 from overlapping win-
dows consisting of 1000 variants. Linkage pruning in this way reduced the number of variants in the putatively
unrelated set to 6642.
We used ADMIXTURE26 and these putatively unlinked variants with all 200 miracidia to determine the pro-
portion of each miracidium’s genome that can be attributed to one of k dierent populations. We tested k = 2–10,
with ten replicates for each k and default cross-validation to determine the k with the lowest cross validation
error (Supplementary Fig.S5).
Principal component analysis (PCA), as implemented in Rs (version 3.5.1)47 ‘SNPrelate’ package48, was applied
to the full variant set to assess how genotype dierences between miracidia contribute to region-wide variability
between samples and villages.
Using all variants, we calculated pairwise genetic distances between miracidia through the distance-based
bitwise.dist function implemented in Rs ‘adegenet’ package49,50 and used distances to construct a neighbor-joining
tree using the Rs ‘apepackage51.
Identication of family clusters and relatedness estimates. To identify highly related samples in
the absence of reliable allele frequency estimates, we used pairwise comparison of shared rare alleles. Rare alleles
were dened as alleles whose minor allele frequency 0.1. Rare allele sharing was calculated between all pairs
of samples using only rare variants and a custom perl script (ndSibClusters.pl; github.com/PollockLaboratory/
Schisto) following
where
and
Pij
is the proportion of shared alleles between individuals i and j, L is the number of loci tested, and k is a
locus for which both individuals i and j have non-missing genotype calls and individual i has a rare variant. To
avoid overestimating relationships because of linked variants, we use the mean proportion of rare alleles shared
generated from 30 replicates of randomly sampling 2000 loci with replacement for each pairwise comparison.
We identied clusters of highly related miracidia such that each miracidium in a cluster shared 0.45 of its rare
alleles with at least one other miracidium in the cluster. Removal of all but one miracidium from each putative
sibling cluster (117 individuals) resulted in a data set of 83 miracidia. e sibling-pruned vcf le, which was used
to prune linked variants, is available at http:// www. E vo l u tiona ryGen omics. com/ Progr amsDa ta/ Schis toGen omics.
(1)
P
ij =
1
L
L
k=1
x
ijk
(2)
xijk =
1 if iand jhave the same genotype at locus k
0.5 if iand jshare one allele at locus k
0 if iand jshare no alleles at locus k
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Calculating posterior probabilities across degrees of relatedness. To generate posterior prob-
ability distributions for each degree of relatedness, we rst estimated mean levels of unrelated allele sharing,
ˆµunrelated =0.04
, as the average pairwise rare allele sharing between individuals from the most geographically
distant villages (n = 35.6km) in the full dataset of 200 miracidia. As analysis of pairwise rare allele sharing by
inter-village distance indicated a statistically signicant decrease in pairwise rare allele sharing as inter-village
distance increased, this was determined to be the best, data-driven estimate. To estimate allele sharing among
sibling miracidia, we began by identifying clusters of miracidia most likely to be siblings (1st degree relatives):
clusters of 3 or more miracidia from the same host and collection timepoint, all with pairwise rare allele sharing
proportionn 0.30 (45 miracidia in 13 clusters). ere were an additional 8 pairs of miracidia within the same
host that are likely siblings but not part of a big enough cluster. e estimated mean,
ˆµsibs =0.44
and variance,
ˆ
σ2
sibs
=
0.30
, of allele sharing were calculated from eligible pairs (n = 60). For intermediate degrees of related-
ness, means (
ˆµdegree
) were estimated by successively halving the distance from sibs to unrelated, and variances
( ˆ
) were estimated by successively halving the sibling variance for each further degree of relatedness, which
will have had twice the number of meioses (e.g., ˆ
µ2
=
(ˆµ
unrelated
µ
sibs
)
2
and ˆ
σ
2
2
=ˆσ
2
sibs
2
). Posterior probabilities
were calculated roughly assuming even prior probabilities for each categorical degree of relatedness from sib-
lings to 5th degree relatives and unrelated, and assuming that allele sharing probabilities for each degree of relat-
edness were distributed normally, i.e.,
N(ˆµdegree,ˆσ
2
degree)
, a reasonable large-sample approximation.
Analysis of non-sibling miracidia. As a safeguard against making conclusions about population struc-
ture using data that may violate assumptions of independence between samples, we used the posterior probabili-
ties of relatedness to identify sibling clusters (see “Identication of family clusters and relatedness estimates” and
Calculating posterior probabilities across degrees of relatedness”) and generated a sibling-pruned dataset that
includes 81 non-sibling miracidia. We used the sibling-pruned dataset to repeat analyses described in “Popula-
tion analyses, namely: ADMIXTURE, PCA, and construction of a neighbor-joining tree. Finally, we subset the
rare-allele sharing described in “Identication of family clusters and relatedness estimates” to include only the
81 non-sibling miracidia and compared the proportions of shared rare alleles between all pairs of remaining
miracidia to the distance between the two villages where members of the pair were collected.
Data availability
Sequences generated during this work have been deposited in the NCBI Sequence Read Archive under BioProject
PRJNA349754. e vcf le used in analysis is available at http:// www. Evolu tiona ryGen omics. com/ Progr amsDa
ta/ Schis toGen omics and custom scripts are available at github.com/PollockLaboratory/Schisto.
Received: 25 June 2020; Accepted: 9 March 2021
References
1. Hotez, P. J., Fenwick, A., Savioli, L. & Molyneux, D. H. Rescuing the bottom billion through control of neglected tropical diseases.
Lancet 373, 1570–1575. https:// doi. org/ 10. 1016/ S0140- 6736(09) 60233-6 (2009).
2. Hampton, T. Collaborative eort targets 17 tropical diseases for control, elimination. JAMA 307, 772 (2012).
3. Vos, T. et al. Years lived with disability (YLDs) for 1160 sequelae of 289 diseases and injuries 1990–2010: A systematic analysis for
the Global Burden of Disease Study 2010. Lancet 380, 2163–2196. https:// doi. org/ 10. 1016/ S0140- 6736(12) 61729-2 (2012).
4. Friedman, J. F., Kanzaria, H. K. & McGarvey, S. T. Human schistosomiasis and anemia: e relationship and potential mechanisms.
Trends Parasitol. 21, 386–392. https:// doi. org/ 10. 1016/j. pt. 2005. 06. 006 (2005).
5. Gryseels, B., Polman, K., Clerinx, J. & Kestens, L. Human schistosomiasis. Lancet 368, 1106–1118. https:// doi. org/ 10. 1016/ S0140-
6736(06) 69440-3 (2006).
6. Li-Juan, Z. et al. Endemic status of schistosomiasis in People’s Republic of China in 2016. Chin. J. Schistosomiasis Control 29,
669–677 (2017).
7. Minggang, C. & Zheng, F. Schistosomiasis control in China. Parasitol. Int. 48, 11–19. https:// doi. org/ 10. 1016/ S1383- 5769(99)
00004-5 (1999).
8. Shou-Pai, M. & Bao-Ruo, S. Schistosomiasis control in the People’s Republic of China. Am. J. Trop. Med. Hyg. 31, 92–99 (1982).
9. Liu, Y. et al. Interruption of schistosomiasis transmission in mountainous and hilly regions with an integrated strategy: A longi-
tudinal case study in Sichuan, China. Infect. Dis. Poverty 6, 1–9. https:// doi. org/ 10. 1186/ s40249- 017- 0290-6 (2017).
10. Wang, L.-D. et al. A strategy to control transmission of Schistosomajaponicum in China. N. Engl. J. Med. 360, 121–128 (2009).
11. Liang, S., Yang, C., Zhong, B. & Qiu, D. Re-emerging schistosomiasis in hilly and mountainous areas of Sichuan, China. Bull. World
Health Organ. 84, 139–144. https:// doi. org/ 10. 2471/ blt. 05. 025031 (2006).
12. Xu, J. et al. Evolution of the national schistosomiasis control programmes in e People’s Republic of China. Adv. Parasitol. 92,
1–38. https:// doi. org/ 10. 1016/ bs. apar. 2016. 02. 001 (2016).
13. Wiegand, R. E. et al. A persistent hotspot of Schistosomamansoni infection in a ve-year randomized trial of praziquantel preventa-
tive chemotherapy strategies. J. Infect. Dis. 216, 1425–1433. https:// doi. org/ 10. 1093/ infdis/ jix496 (2017).
14. Carlton, E. J., Hubbard, A., Wang, S. & Spear, R. C. Repeated Schistosomajaponicum infection following treatment in two cohorts:
Evidence for host susceptibility to helminthiasis?. PLoS Negl. Trop. Dis. 7, e2098. https:// doi. org/ 10. 1371/ journ al. pntd. 00020 98
(2013).
15. Sun, L. P. et al. Approaches being used in the national schistosomiasis elimination programme in China: A review. Infect. Dis.
Poverty 6, 1–9. https:// doi. org/ 10. 1186/ s40249- 017- 0271-9 (2017).
16. Yin, M. et al. Temporal genetic diversity of Schistosomajaponicum in two endemic sites in China revealed by microsatellite markers.
Parasites Vectors 9, 1–5. https:// doi. org/ 10. 1186/ s13071- 016- 1326-7 (2016).
17. Rudge, J. W. et al. Parasite genetic dierentiation by habitat type and host species: Molecular epidemiology of Schistosomajaponi-
cum in hilly and marshland areas of Anhui Province, China. Mol. Ecol. 18, 2134–2147. https:// doi. org/ 10. 1111/j. 1365- 294X. 2009.
04181.x (2009).
18. Barbosa, L. M. et al. Characteristics of the human host have little inuence on which local Schistosomamansoni populations are
acquired. PLoS Negl. Trop. Dis. 7, 1–9. https:// doi. org/ 10. 1371/ journ al. pntd. 00025 72 (2013).
Content courtesy of Springer Nature, terms of use apply. Rights reserved

Vol:.(1234567890)
Scientic Reports | (2021) 11:6884 | 
www.nature.com/scientificreports/
19. Gower, C. M. et al. Population genetic structure of Schistosomamansoni and Schistosomahaematobium from across six sub-Saharan
African countries: Implications for epidemiology, evolution and control. Ac ta Trop. 128, 261–274. https:// doi. org/ 10. 1016/j. actat
ropica. 2012. 09. 014 (2013).
20. Prugnolle, F. et al. Dispersal in a parasitic worm and its two hosts: Consequence for local adaptation. Evolution 59, 296–303 (2005).
21. Steinauer, M. L., Agola, L. E., Mwangi, I. N., Mkoji, G. M. & Loker, E. S. Molecular epidemiology of Schistosomamansoni: A robust,
high-throughput method to assess multiple microsatellite markers from individual miracidia. Infect. Genet. Evol. 8, 68–73. https://
doi. org/ 10. 1016/j. meegid. 2007. 10. 004 (2008).
22. Carlton, E. J., Liu, Y., Zhong, B., Hubbard, A. & Spear, R. C. Associations between Schistosomiasis and the use of human waste as
an agricultural fertilizer in China. PLoS Negl. Trop. Dis. 9, e0003444. https:// doi. org/ 10. 1371/ journ al. pntd. 00034 44 (2015).
23. Carlton, E. J., Bates, M. N., Zhong, B., Seto, E. Y. W. & Spear, R. C. Evaluation of mammalian and intermediate host surveillance
methods for detecting schistosomiasis reemergence in Southwest China. PLoS Negl. Trop. Dis. 5, e987. https:// doi. org/ 10. 1371/
journ al. pntd. 00009 87 (2011).
24. Shortt, J. A. et al. Whole genome amplication and reduced-representation genome sequencing of Schistosomajaponicum miracidia.
PLoS Negl. Trop. Dis. 11, e0005292. https:// doi. org/ 10. 1371/ journ al. pntd. 00052 92 (2017).
25. Peterson, B. K., Weber, J. N., Kay, E. H., Fisher, H. S. & Hoekstra, H. E. Double digest RADseq: An inexpensive method for de novo
SNP discovery and genotyping in model and non-model species. PLoS ONE 7, e37135. https:// doi. org/ 10. 1371/ journ al. pone. 00371
35 (2012).
26. Alexander, D. H., Novembre, J. & Lange, K. Fast model-based estimation of ancestry in unrelated individuals. Genome Res. 19,
1655–1664. https:// doi. org/ 10. 1101/ gr. 094052. 109 (2009).
27. Seto, E. Y. W. et al. Toward sustainable and comprehensive control of Schistosomiasis in China: Lessons from Sichuan. PLoS Negl.
Trop. Dis. 5, e1372. https:// doi. org/ 10. 1371/ journ al. pntd. 00013 72 (2011).
28. Xie, F. et al. Life span and cercaria shedding of schistosome-infected snails in mountain region of Yunnan. Chin. J. Parasitol. Parasit.
Dis. 8, 4–7 (1990).
29. Colley, D. G., Bustinduy, A. L., Secor, W. E. & King, C. H. Human schistosomiasis. Lancet 383, 2253–2264. https:// doi. org/ 10. 1016/
S0140- 6736(13) 61949-2 (2014).
30. Catalano, S. et al. Multihost transmission of Schistosomamansoni in Senegal, 2015–2018. Emerg. Infect. Dis. 26, 1234–1242. https://
doi. org/ 10. 3201/ eid26 06. 200107 (2020).
31. Norton, A. J. et al. Genetic consequences of mass human chemotherapy for Schistosomamansoni: Population structure pre- and
post-praziquantel treatment in Tanzania. Am. J. Trop. Med. Hyg. 83, 951–957. https:// doi. org/ 10. 4269/ ajtmh. 2010. 10- 0283 (2010).
32. Webster, J. P. et al. Parasite population genetic contributions to the Schistosomiasis Consortium for Operational Research and
Evaluation within Sub-Saharan Africa. Am. J. Trop. Med. Hyg. 103, 80–91. https:// doi. org/ 10. 4269/ ajtmh. 19- 0827 (2020).
33. Faust, C. L. et al. Two-year longitudinal survey reveals high genetic diversity of Schistosomamansoni with adult worms surviv-
ing praziquantel treatment at the start of mass drug administration in Uganda. Parasit. Vectors 12, 607. https:// doi. org/ 10. 1186/
s13071- 019- 3860-6 (2019).
34. King, C. H. et al. Utility of repeated praziquantel dosing in the treatment of schistosomiasis in high-risk communities in Africa:
A systematic review. PLoS Negl. Trop. Dis. 5, e1321. https:// doi. org/ 10. 1371/ journ al. pntd. 00013 21 (2011).
35. Farrell, S. H. & Anderson, R. M. Helminth lifespan interacts with non-compliance in reducing the eectiveness of anthelmintic
treatment. Parasit. Vectors 11, 66. https:// doi. org/ 10. 1186/ s13071- 018- 2670-6 (2018).
36. Steinauer, M. L., Blouin, M. S. & Criscione, C. D. Applying evolutionary genetics to schistosome epidemiology. Infect. Genet. Evol.
10, 433–443. https:// doi. org/ 10. 1016/j. meegid. 2010. 02. 007 (2010).
37. Luo, F. et al. An improved genome assembly of the uke Schistosoma japonicum. PLoS Negl. Trop. Dis. https:// doi. org/ 10. 1371/
journ al. pntd. 00076 12 (2019).
38. Catchen, J., Hohenlohe, P. A., Bassham, S., Amores, A. & Cresko, W. A. Stacks: An analysis tool set for population genomics. Mol.
Ecol. 22, 3124–3140. https:// doi. org/ 10. 1111/ mec. 12354 (2013).
39. Zerlotini, A. et al. SchistoDB: An updated genome resource for the three key schistosomes of humans. Nucleic Acids Res. 41,
728–731. https:// doi. org/ 10. 1093/ nar/ gks10 87 (2013).
40. Zhou, Y. et al. e Schistosomajaponicum genome reveals features of host–parasite interplay. Nature 460, 345–351. https:// doi. org/
10. 1038/ natur e08140. e (2009).
41. Li, H. & Durbin, R. Fast and accurate short read alignment with Burrows–Wheeler transform. Bioinformatics 25, 1754–1760.
https:// doi. org/ 10. 1093/ bioin forma tics/ btp324 (2009).
42. DePristo, M. A. et al. A framework for variation discovery and genotyping using next-generation DNA sequencing data. Nat.
Genet. 43, 491–498. https:// doi. org/ 10. 1038/ ng. 806.A (2011).
43. McKenna, A. et al. e Genome Analysis Toolkit: A MapReduce framework for analyzing next-generation DNA sequencing data.
Genome Res. 20, 1297–1303 (2010).
44. Van der Auwera, G. A. et al. From fastQ data to high-condence variant calls: e genome analysis toolkit best practices pipeline.
Curr. Protoc. Bioinform. https:// doi. org/ 10. 1002/ 04712 50953. bi111 0s43 (2013).
45. Quinlan, A. R. BEDTools: e Swiss-Army tool for genome feature analysis. Curr. Protoc. Bioinform. Suppl 47, 1–34. https:// doi.
org/ 10. 1002/ 04712 50953. bi111 2s47 (2014).
46. Purcell, S. et al. PLINK: A tool set for whole-genome association and population-based linkage analyses. Am. J. Hum. Genet. 81,
559–575. https:// doi. org/ 10. 1086/ 519795 (2007).
47. R: A Language and Environment for Statistical Computing (R Foundation for Statistical Computing, 2018).
48. Zheng, X. et al. A high-performance computing toolset for relatedness and principal component analysis of SNP data. Bioinformat-
ics 28, 3326–3328. https:// doi. org/ 10. 1093/ bioin forma tics/ bts606 (2012).
49. Jombart, T. adegenet: A R package for the multivariate analysis of genetic markers. Bioinformatics 24, 1403–1405. htt ps:// doi. org/
10. 1093/ bioin forma tics/ btn129 (2008).
50. Jombart, T. & Ahmed, I. adegenet 1.3-1: New tools for the analysis of genome-wide SNP data. Bioinformatics 27, 3070–3071. https://
doi. org/ 10. 1093/ bioin forma tics/ btr521 (2011).
51. Paradis, E., Claude, J. & Strimmer, K. APE: Analyses of phylogenetics and evolution in R language. Bioinformatics 20, 289–290.
https:// doi. org/ 10. 1093/ bioin forma tics/ btg412 (2004).
52. ArcMap v. 10.6 (Environmental Systems Research Institute, 2019).
Acknowledgements
We thank the members of the Sichuan Centers of Disease Control and the local county anti-schistosomiasis sta-
tions for their assistance in collecting parasite samples and related eld data. is work was supported by fund-
ing from the NIH (R21 AI115288 from National Institute of Allergy and Infectious Disease and R01 AI134673)
to EJC as principal investigator and YL, BZ, TAC, and DDP as co-investigators.LET wasfunded through the
Colorado Biomedical Informatics Training Program (T15 LM009451).
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Scientic Reports | (2021) 11:6884 | 
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Author contributions
T.A.C., E.J.C., and D.D.P. conceived and supervised the study, also serving as project administrators. J.A.S., T.A.C.,
E.J.C., and D.D.P. designed the experiment. J.A.S. and D.D.P. developed soware for data analysis. L.E.T. vali-
dated the data and results. J.A.S., L.E.T., N.R.H., Z.L.N., D.R.S., B.W.P., T.A.C., and D.D.P. executed the analyses.
Funding and other resources for this study were provided by Y.L., B.Z., T.A.C., E.J.C., and D.D.P. J.A.S., L.E.T.,
T.A.C., and D.D.P. ensured data was properly curated and made publicly available. e original dra of this
manuscript was prepared by J.A.S., E.J.C., and D.D.P. J.A.S., L.E.T., N.R.H., Z.L.N., D.R.S., B.W.P., T.A.C., and
D.D.P. contributed to data visualization. All authors reviewed the manuscript prior to submission.
Competing interests
e authors declare no competing interests.
Additional information
Supplementary Information e online version contains supplementary material available at https:// doi. org/
10. 1038/ s41598- 021- 86287-y.
Correspondence and requests for materials should be addressed to D.D.P.
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... Various local scale applications of helminth population genomics have included studying the potential for transmission foci, the potential impacts of chemotherapeutic control measures and assessment of reservoir hosts (table 2). An example addressing transmission dynamics is provided by Shortt et al. (2021) where miracidia of Schistosoma japonicum were collected from 12 villages (maximum distance ∼25 km) in Sichuan, China, in 2007China, in , 2008China, in , 2010 and 2016. Using model-based and non-model-based clustering analyses, individuals from the same village largely belonged to the same cluster, regardless of the timeperiod sampled. ...
... Sibling miracidia were also found in pre-praziquantel and post-praziquantel treatment of the same host, indicating that individuals likely retained infections of adult flukes. Collectively, the results of Shortt et al. (2021) parallel findings from a microsatellite-based landscape genetics study on the roundworm A. lumbricoides in that there are local parasite transmission foci and that these foci are stable over time and after drug treatment. ...
... At the individual host level, Berger et al. (2021) did not find evidence of highly related S. mansoni miracidia from individuals in shoreline villages of Lake Victoria. Vianney et al. (2022), however, did find some related S. mansoni miracidia from island villages of Lake Victoria using the relatedness measure of Shortt et al. (2021). The relatedness measure of Shortt et al. (2021) is a withinstudy relative measure as the proportion of shared alleles cut-off to determine relatedness differs in Vianney et al. (2022); thus, a direct comparison between the S. japonicum and S. mansoni studies is not possible. ...
Article
Full-text available
Next generation sequencing technologies have facilitated a shift from a few targeted loci in population genetic studies to whole genome approaches. Here, we review the types of questions and inferences regarding the population biology and evolution of parasitic helminths being addressed within the field of population genomics. Topics include parabiome, hybridization, population structure, loci under selection and linkage mapping. We highlight various advances, and note the current trends in the field, particularly a focus on human-related parasites despite the inherent biodiversity of helminth species. We conclude by advocating for a broader application of population genomics to reflect the taxonomic and life history breadth displayed by helminth parasites. As such, our basic knowledge about helminth population biology and evolution would be enhanced while the diversity of helminths in itself would facilitate population genomic comparative studies to address broader ecological and evolutionary concepts.
... WGS from individual miracidia and cercaria, the readily available schistosome life stages, is challenging due to the low quantity of DNA available from these physically small samples [(15, 26); see also discussion in Rey et al. (6)]. Recent advances that use whole genome amplification (WGA) ameliorate this challenge, and thus substantially increase the feasibility of genomic surveillance by enabling WGS of individual parasites (12,27,28). Low-input DNA genomic library preparation approaches that accomplish amplification through PCR have also shown promising results using schistosome eggs or larval stage samples (29). ...
... A number of studies that have used WGS to sequence DNA from miracidia seem to have little host contamination (12,27,28), suggesting minimal off-target sequencing of host DNA using filtration and washing protocols to separate miracidia from host stool, as is used for the miracidial hatching test in China (30). However, other studies (13) have reported higher rates of contamination (based on higher fractions of genome sequencing reads that do not map to schistosome reference genomes), suggesting contamination may be more of an issue in some cases. ...
... The biology of schistosomes requires particular attention when considering experimental design for genomic scan approaches to detect and interpret patterns of selection. Schistosomes are overall genetically diverse, but they can be far more closely related in small geographic areas such as in areas of re-emergence or hotspots (6,12,27,90). This makes sense biologically because of the large number of eggs a single worm pair can produce, combined with the clonal nature and large numbers of cercaria produced from a single snail intermediate host. ...
Article
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Schistosomiasis is a neglected tropical disease caused by multiple parasitic Schistosoma species, and which impacts over 200 million people globally, mainly in low- and middle-income countries. Genomic surveillance to detect evidence for natural selection in schistosome populations represents an emerging and promising approach to identify and interpret schistosome responses to ongoing control efforts or other environmental factors. Here we review how genomic variation is used to detect selection, how these approaches have been applied to schistosomes, and how future studies to detect selection may be improved. We discuss the theory of genomic analyses to detect selection, identify experimental designs for such analyses, and review studies that have applied these approaches to schistosomes. We then consider the biological characteristics of schistosomes that are expected to respond to selection, particularly those that may be impacted by control programs. Examples include drug resistance, host specificity, and life history traits, and we review our current understanding of specific genes that underlie them in schistosomes. We also discuss how inherent features of schistosome reproduction and demography pose substantial challenges for effective identification of these traits and their genomic bases. We conclude by discussing how genomic surveillance for selection should be designed to improve understanding of schistosome biology, and how the parasite changes in response to selection.
... www.nature.com/scientificreports/ Population genetic analyses can provide insight into transmission patterns and responses by schistosome populations to control programs [7][8][9] . Schistosoma mansoni has a multitiered population structure. ...
... Schistosomiasis persists throughout the world and is now spreading from rural to urban areas despite control efforts, including successful treatment using the drug praziquantel 6,19 . Methods to detect the sources of recurring infections and the spread of new infections are of paramount importance, and genetic analysis has become prominent in the epidemiological toolbox 9 . In this study, we analyze allele frequency profiles calculated from fourteen microsatellite loci in Schistosoma mansoni infrapopulations existing in three communities in the state of Bahia, Brazil. ...
... Gene identity varies substantially among infrapopulations in the same community, although the average gene identity in the three communities is roughly the same, 0.348-0.357. Worm burden is a principal determinant of gene identity in infrapopulations, although there are contributing factors such as inbreeding and genetic kinship among the worms within an infrapopulation 8,9,13 . The high variability of gene identity among infrapopulations within a community is important because migration of S. mansoni to new locations involves human feces which transfer fertilized eggs from an entire infrapopulation. ...
Article
Full-text available
Patterns of diversity in pathogen genomes provide a window into the spatiotemporal spread of disease. In this study, we tested the hypothesis that Schistosoma mansoni parasites form genetic clusters that coincide with the communities of their human hosts. We also looked for genetic clustering of parasites at the sub-community level. Our data consists of 14 microsatellite DNA markers, typed from pooled DNA samples from N=254 N = 254 infected individuals living in three Brazilian communities. We found a one-to-one correspondence between genetic clusters found by K-means cluster analysis and communities when K=3K = 3 K = 3 . These clusters are also easily identified in a neighbor-joining tree and principal coordinates plots. K-means analysis with K>3K > 3 K > 3 also reveals genetic clusters of parasites at the sub-community level. These sub-clusters also appear on the neighbor-joining tree and principal coordinates plots. A surprising finding is a genetic relationship between subgroups in widely separated human communities. This connection suggests the existence of common transmission sites that have wide influence. In summary, the genetic structure of S. mansoni in Brazil juxtaposes local isolation that is occasionally broken by long-range migration. Permanent eradication of schistosomes will require both local efforts and the identification of regional infection reservoirs.
... populations have changed following MDA [22][23][24] , these have been restricted to a limited number of molecular markers. By contrast, few studies have analysed whole-genome or exome sequence data from populations of S. mansoni 17,25 or other schistosomes 17,[25][26][27] . ...
... As expected, our results show that MDA targeting school-age children has had a limited impact on the parasite population size or diversity at the community level. Our finding that the population of S. mansoni in Mayuge remains essentially panmictic is in contrast to Schistosoma japonicum populations in China, where one sign that elimination efforts have drastically reduced parasite circulation is the high level of population structure and relatedness between parasites from different hosts 27,103 . Together, these results suggest we are a long way from dramatically reducing schistosome transmission in this area of high infection prevalence and intensity. ...
Article
Full-text available
Control and elimination of the parasitic disease schistosomiasis relies on mass administration of praziquantel. Whilst these programmes reduce infection prevalence and intensity, their impact on parasite transmission and evolution is poorly understood. Here we examine the genomic impact of repeated mass drug administration on Schistosoma mansoni populations with documented reduced praziquantel efficacy. We sequenced whole-genomes of 198 S. mansoni larvae from 34 Ugandan children from regions with contrasting praziquantel exposure. Parasites infecting children from Lake Victoria, a transmission hotspot, form a diverse panmictic population. A single round of treatment did not reduce this diversity with no apparent population contraction caused by long-term praziquantel use. We find evidence of positive selection acting on members of gene families previously implicated in praziquantel action, but detect no high frequency functionally impactful variants. As efforts to eliminate schistosomiasis intensify, our study provides a foundation for genomic surveillance of this major human parasite.
... It remains unknown if these unique genetic traits are related to differences in transmission and disease epidemiology, however, it is certainly clear that Zanzibari S. haematobium populations are not comparable to those from the African mainland. Increased sample sets and population genomic level analyses (Shortt et al., 2021) would provide further insights into these genetic traits and if they impact control interventions. ...
Chapter
Zanzibar is among the few places in sub-Saharan Africa where interruption of Schistosoma transmission seems an achievable goal. Our systematic review identifies and discusses milestones in schistosomiasis research, control and elimination efforts in Zanzibar over the past 100 years. The search in online databases, libraries, and the World Health Organization Archives revealed 153 records published between May 1928 and August 2022. The content of records was summarised to highlight the pivotal work leading towards urogenital schistosomiasis elimination and remaining research gaps. The greatest achievement following 100 years of schistosomiasis interventions and research is undoubtedly the improved health of Zanzibaris, exemplified by the reduction in Schistosoma haematobium prevalence from>50% historically down to<5% in 2020, and the absence of severe morbidities. Experiences from Zanzibar have contributed to global schistosomiasis guidelines, whilst also revealing challenges that impede progression towards elimination. Challenges include: transmission heterogeneity requiring micro-targeting of interventions, post-treatment recrudescence of infections in transmission hotspots, biological complexity of intermediate host snails, emergence of livestock Schistosoma species complicating surveillance whilst creating the risk for interspecies hybridisation, insufficient diagnostics performance for light intensity infections and female genital schistosomiasis, and a lack of acceptable sanitary alternatives to freshwater bodies. Our analysis of the past revealed that much can be achieved in the future with practical implementation of integrated interventions, alongside operational research. With continuing national and international commitments, interruption of S. haematobium transmission across both islands is within reach by 2030, signposting the future demise of urogenital schistosomiasis across other parts of sub-Saharan Africa.
... There are several countries and areas that have made great progress in the fight against schistosomiasis in the past and may aim to achieve full interruption of transmission in the next few years [6][7][8][9][10]. These countries will need clear guidance on which intervention strategies to apply, which population groups to target, which diagnostics to use, and at what thresholds to change and adapt their strategies [11][12][13]. ...
Article
Full-text available
Background Global elimination of schistosomiasis as a public health problem is set as target in the new World Health Organization’s Neglected Tropical Diseases Roadmap for 2030. Due to a long history of interventions, the Zanzibar islands of Tanzania have reached this goal since 2017. However, challenges occur on the last mile towards interruption of transmission. Our study will investigate new tools and strategies for breaking schistosomiasis transmission. Methods The study is designed as an intervention study, documented through repeated cross-sectional surveys (2020–2024). The primary endpoint will be the sensitivity of a surveillance-response approach to detect and react to outbreaks of urogenital schistosomiasis over three years of implementation. The surveys and multi-disciplinary interventions will be implemented in 20 communities in the north of Pemba island. In low-prevalence areas, surveillance-response will consist of active, passive and reactive case detection, treatment of positive individuals, and focal snail control. In hotspot areas, mass drug administration, snail control and behaviour change interventions will be implemented. Parasitological cross-sectional surveys in 20 communities and their main primary schools will serve to adapt the intervention approach annually and to monitor the performance of the surveillance-response approach and impact of interventions. Schistosoma haematobium infections will be diagnosed using reagent strips and urine filtration microscopy, and by exploring novel point-of-care diagnostic tests. Discussion Our study will shed light on the field applicability and performance of novel adaptive intervention strategies, and standard and new diagnostic tools for schistosomiasis elimination. The evidence and experiences generated by micro-mapping of S. haematobium infections at community level, micro-targeting of new adaptive intervention approaches, and application of novel diagnostic tools can guide future strategic plans for schistosomiasis elimination in Zanzibar and inform other countries aiming for interruption of transmission. Trial registration ISRCTN, ISCRCTN91431493. Registered 11 February 2020, https://www.isrctn.com/ISRCTN91431493
Preprint
Full-text available
Soil-transmitted helminths (STHs) are intestinal pathogens affecting over a billion people worldwide. STH control relies on microsopy-based diagnostics to monitor parasite prevalence and enable post-treatment surveillance, however, molecular diagnostics are rapidly being developed due to increased sensitivity, particularly in low-STH-prevalence settings. The genetic diversity of helminths and its potential impact on molecular diagnostics remains unclear. Using low-coverage genome sequencing, we assessed the presence of STHs in worm, faecal and purified egg samples from 27 countries, identifying differences in the genetic connectivity and diversity of STH-positive samples across regions and cryptic diversity between closely related human- and pig-infective species. We defined substancial copy number and sequence variants in current diagnostic targets and validated the impact of genetic variants on qPCR diagnostics using in vitro assays. Our study provides insights into the diversity and genomic epidemiology of STHs, highlighting challenges and opportunities for developing molecular diagnostics needed to support STH control efforts.
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Full-text available
The global community has adopted ambitious goals to eliminate schistosomiasis as a public health problem, and new tools are needed to achieve them. Mass drug administration programs, for example, have reduced the burden of schistosomiasis, but the identification of hotspots of persistent and reemergent transmission threaten progress toward elimination and underscore the need to couple treatment with interventions that reduce transmission. Recent advances in DNA sequencing technologies make whole-genome sequencing a valuable and increasingly feasible option for population-based studies of complex parasites such as schistosomes. Here, we focus on leveraging genomic data to tailor interventions to distinct social and ecological circumstances. We consider two priority questions that can be addressed by integrating epidemiological, ecological, and genomic information: (1) how often do non-human host species contribute to human schistosome infection? and (2) what is the importance of locally acquired versus imported infections in driving transmission at different stages of elimination? These questions address processes that can undermine control programs, especially those that rely heavily on treatment with praziquantel. Until recently, these questions were difficult to answer with sufficient precision to inform public health decision-making. We review the literature related to these questions and discuss how whole-genome approaches can identify the geographic and taxonomic sources of infection, and how such information can inform context-specific efforts that advance schistosomiasis control efforts and minimize the risk of reemergence.
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Populations within schistosomiasis control areas, especially those in Africa, are recommended to receive regular mass drug administration (MDA) with praziquantel (PZQ) as the main strategy for controlling the disease. The impact of PZQ treatment on schistosome genetics remains poorly understood, and is limited by a lack of high-resolution genetic data on the population structure of parasites within these control areas. We generated whole-genome sequence data from 174 individual miracidia collected from both children and adults from fishing communities on islands in Lake Victoria in Uganda that had received either annual or quarterly MDA with PZQ over four years, including samples collected immediately before and four weeks after treatment. Genome variation within and between samples was characterised and we investigated genomic signatures of natural selection acting on these populations that could be due to PZQ treatment. The parasite population on these islands was more diverse than found in nearby villages on the lake shore. We saw little or no genetic differentiation between villages, or between the groups of villages with different treatment intensity, but slightly higher genetic diversity within the pre-treatment compared to post-treatment parasite populations. We identified classes of genes significantly enriched within regions of the genome with evidence of recent positive selection among post-treatment and intensively treated parasite populations. The differential selection observed in post-treatment and pre-treatment parasite populations could be linked to any reduced susceptibility of parasites to praziquantel treatment.
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Background: A key component of schistosomiasis control is mass drug administration with praziquantel. While control interventions have been successful in several endemic regions, mass drug administration has been less effective in others. Here we focus on the impact of repeated praziquantel treatment on the population structure and genetic diversity of Schistosoma mansoni. Methods: We examined S. mansoni epidemiology, population genetics, and variation in praziquantel susceptibility in parasites isolated from children across three primary schools in a high endemicity region at the onset of the Ugandan National Control Programme. Children were sampled at 11 timepoints over two years, including one week and four weeks post-praziquantel treatment to evaluate short-term impacts on clearance and evidence of natural variation in susceptibility to praziquantel. Results: Prevalence of S. mansoni was 85% at baseline. A total of 3576 miracidia larval parasites, isolated from 203 individual children, were genotyped at seven loci. Overall, genetic diversity was high and there was low genetic differentiation, indicating high rates of parasite gene flow. Schistosome siblings were found both pre-treatment and four weeks post-treatment, demonstrating adult worms surviving treatment and natural praziquantel susceptibility variation in these populations at the beginning of mass drug administration. However, we did not find evidence for selection on these parasites. While genetic diversity decreased in the short-term (four weeks post-treatment), diversity did not decrease over the entire period despite four rounds of mass treatment. Furthermore, within-host genetic diversity was affected by host age, host sex, infection intensity and recent praziquantel treatment. Conclusions: Our findings suggest that praziquantel treatments have short-term impacts on these parasite populations but impacts were transient and no long-term reduction in genetic diversity was observed. High gene flow reduces the likelihood of local adaptation, so even though parasites surviving treatment were observed, these were likely to be diluted at the beginning of the Ugandan National Control Programme. Together, these results suggest that MDA in isolation may be insufficient to reduce schistosome populations in regions with high genetic diversity and gene flow.
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Background: The success of mass drug administration programmes targeting the soil-transmitted helminths and schistosome parasites is in part dependent on compliance to treatment at sequential rounds of mass drug administration (MDA). The impact of MDA is vulnerable to systematic non-compliance, defined as a portion of the eligible population remaining untreated over successive treatment rounds. The impact of systematic non-compliance on helminth transmission dynamics - and thereby on the number of treatment rounds required to interrupt transmission - is dependent on the parasitic helminth being targeted by MDA. Results: Here, we investigate the impact of adult parasite lifespan in the human host and other factors that determine the magnitude of the basic reproductive number R 0 , on the number of additional treatment rounds required in a target population, using mathematical models of Ascaris lumbricoides and Schistosoma mansoni transmission incorporating systematic non-compliance. Our analysis indicates a strong interaction between helminth lifespan and the impact of systematic non-compliance on parasite elimination, and confirms differences in its impact between Ascaris and the schistosome parasites in a streamlined model structure. Conclusions: Our analysis suggests that achieving reductions in the level of systematic non-compliance may be of particular benefit in mass drug administration programmes treating the longer-lived helminth parasites, and highlights the need for improved data collection in understanding the impact of compliance.
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Background: Persistent hotspots have been described following mass drug administration (MDA) for the control of schistosomiasis, but have not been studied during the course of a multi-year MDA program. Methods: In data from a five-year study of school-based and village-wide preventive chemotherapy strategies for Schistosoma mansoni, spatial scan statistics were used to find infection hotspots in three populations: 5-8 year olds, 9-12 year olds, and adults. Negative binomial regression was used to analyze changes from baseline and ROC analyses were used to predict which villages would reach prevalence and intensity endpoints. Results: We identified a persistent hotspot, not associated with study arm, where S. mansoni infection prevalence and intensity did not decrease as much as in villages outside the hotspot. Significant differences from baseline were realized after one year of MDA; we did not identify factors that moderated this relationship. Villages meeting specified endpoints at year 5 were predicted from prior year data with moderately high sensitivity and specificity. Conclusions: MDA strategies were less effective at reducing prevalence and intensity in the hotspot compared to other villages. Villages that reached year 5 endpoints could be detected earlier providing the opportunity to amend intervention strategies.
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Background Schistosomiasis remains a major public health concern in China. Since 2004, an integrated strategy was developed to control the transmission of Schistosoma japonicum in China. However, the long-term effectiveness of this integrated strategy for the interruption of schistosomiasis transmission remains unknown in the mountainous and hilly regions of China until now. This longitudinal study aims to evaluate the effectiveness of the integrated strategy on transmission interruption of schistosomiasis in Sichuan Province from 2005 through 2014. Methods The data regarding replacement of bovines with machines, improved sanitation, access to clean water, construction of public toilets and household latrines, snail control, chemotherapy, and health education were captured from the annual report of the schistosomiasis control programmes in Sichuan Province from 2005 to 2014, and S. japonicum infection in humans, bovines and snails were estimated to evaluate the effectiveness of the integrated strategy. ResultsDuring the 10-year period from 2005 through 2014, a total of 536 568 machines were used to replace bovines, and 3 284 333 household lavatories and 15 523 public latrines were built. Tap water was supplied to 19 116 344 residents living in the endemic villages. A total of 230 098 hm2 snail habitats were given molluscicide treatment, and 357 233 hm2 snail habitats received environmental improvements. There were 7 268 138 humans and 840 845 bovines given praziquantel chemotherapy. During the 10-year study period, information, education and communication (IEC) materials were provided to village officers, teachers and schoolchildren. The 10-year implementation of the integrated strategy resulted in a great reduction in S. japonicum infection in humans, bovines and snails. Since 2007, no acute infection was detected, and no schistosomiasis cases or infected bovines were identified since 2012. In addition, the snail habitats reduced by 62.39% in 2014 as compared to that in 2005, and no S. japonicum infection was identified in snails since 2007. By 2014, 88.9% of the endemic counties achieved the transmission interruption of schistosomiasis and transmission control of schistosmiasis was achieved in the whole province in 2008. Conclusion The government-directed and multi-department integrated strategy is effective for interrupting the transmission of schistosomiasis in the mountainous and hilly regions of China.
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This report presents the endemic status of schistosomiasis in the People's Republic of China at national level in 2016, and analyzes the data collected from the national schistosomiasis prevention and control system and 454 national schistosomiasis surveillance sites. Among the 12 provinces (municipality and autonomous region) of endemic of schistosomiasis japonica in P. R. China, 5 provinces (municipality and autonomous region), i.e., Shanghai, Zhejiang, Fujian, Guangdong and Guangxi, had achieved elimination, and 7 provinces of Sichuan, Yunnan, Jiangsu, Hubei, Anhui, Jiangxi and Hunan had achieved transmission control by the end of 2016. There are 451 endemic counties (cities, districts) covering 257 million people, specifically including 29 692 endemic villages of 69.39 million people at risk. Among the 451 endemic counties (cities, districts), 35.25 % (159/451), 42.35% (191/451) and 22.39% (101/451) reached the criteria of elimination, transmission interruption and transmission control, respectively in 2016. By the end of 2016, it was estimated of 54 454 infections of schistosome, decreased by 29.46% compared with 77 194 in 2015. No acute schistosomiasis case was reported in 2016. There were 30 573 advanced schistosomiasis cases documented in 2016. A total of 8 500 710 individuals received schistosomiasis examinations and 600 individuals were parasitologically diagnosed, decreased by 83.36% compared with 3 606 in 2015. TheOncomelania hupensissnail survey was performed in 22 140 endemic villages andO. hupensissnails were found in 7 106 villages, accounting for 32.109% of the total villages, with 20 newly detected villages with snails. The snail survey covered area of 813 963.91 hm2and snails were found in an area of 235 096.04 hm2, including a newly detected area of 1 346.48 hm2. No schistosome-infected snails were found in 2016. A total of 881 050 bovines were raised in the schistosomiasis endemic area. Of them, 510 468 bovines received examinations, resulting in 8 schistosome-infected bovines. There were 147 642 schistosomiasis cases receiving drug treatment in 2016, with 2 303 555 individuals undergoing expanded chemotherapy; there were 9 bovines with schistosomiasis receiving drug treatment, with 439 857 bovines undergoing expanded chemotherapy; a total of 139 483.84 hm2area with snail control by using molluscicides, with actual molluscicide-treated area of 73 941.75 hm2; and 3 101.52 hm2snail habitants were treated by environmental modification. Based on the data from the 454 national schistosomiasis surveillance sites, the meanSchistosoma japonicuminfection rate was 0.02% and 0.0078% in humans and bovines, respectively. No schistosome-infected snails were found in all the surveillance sites. The results demonstrate a decline in the endemicity of schistosomiasis in P. R. China compared with the level of 2015. However, the distribution area of snails in China is still large and the infection source of schistosomiasis still exists to some extent in some endemic areas; in some regions, the task to reach the standard of transmission interruption is still arduous. There are still objective factors of epidemic and transmission and risk factors of endemic reversal and rebound for schistosomiasis. So, further control and effective surveillance as well as accurate prevention and control should be implemented to promote the elimination process on schistosomiasis in P. R. China.