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. 2019 Sep 2;12:427. doi: 10.1186/s13071-019-3667-5

Urogenital schistosomiasis and risk factors of infection in mothers and preschool children in an endemic district in Zimbabwe

Masceline Jenipher Mutsaka-Makuvaza 1,2, Zvifadzo Matsena-Zingoni 2,3, Agnes Katsidzira 4, Cremance Tshuma 5, Nyasha Chin’ombe 1, Xiao-Nong Zhou 6, Bonnie Webster 7, Nicholas Midzi 1,
PMCID: PMC6721289  PMID: 31477172

Abstract

Background

To design appropriate schistosomiasis control programmes that include women and preschool-aged children (PSAC) it is essential to assess their disease profile and the risk factors predisposing them to infection. This study aimed to determine the prevalence of urogenital schistosomiasis and the risk factors of infection among PSAC and their caregivers in an endemic area of Zimbabwe.

Methods

A cross-sectional study involving screening for urogenital schistosomiasis infections and treatment of 860 participants [535 children aged ≤ 5 years and 325 caregivers (≥ 15 years)] was carried out in five communities, namely Chihuri, Mupfure, Chakondora, Nduna and Kaziro, in February 2016. Haematuria was recorded for each participant and urine filtration was performed to determine the presence and infection intensity of Schistosoma haematobium. A pre-tested questionnaire was administered to the caregivers seeking knowledge, practices and perceptions regarding schistosomiasis. Data analysis was performed using descriptive statistics and logistic regression.

Results

Overall 132 (15.4%) of the 860 participants had S. haematobium infections. Among these, 61 (18.7%) of the 325 caregivers and 71 (13.3%) of the 535 children were infected. The infection prevalence was significantly different between caregivers and PSAC (χ2 = 4.7040, df = 1, P = 0.030). Children whose caregivers used river water for bathing were more likely to be infected compared to children whose caregivers used protected well water (OR: 2.2, 95% CI: 1.3–3.7). The risks of being infected with schistosomiasis were higher in children whose caregivers were infected compared to children whose caregivers had no infection (AOR: 3.9, 95% CI: 1.7–8.6). In caregivers, those who bathed in river water were at higher risk of schistosomiasis infection compared to those who used water from a protected well (AOR: 3.0, 95% CI: 1.4–6.4).

Conclusions

According to the World Health Organization guidelines, the observed overall prevalence of urogenital schistosomiasis qualifies this area as a moderate risk area requiring mass chemotherapy once every two years. Water contact practices of caregivers, and their perceptions and knowledge regarding schistosomiasis are risk factors for infection in both themselves and PSAC. Thus, disease control efforts targeting caregivers or PSAC should include health education and provision of alternative clean and safe water sources.

Keywords: Schistosoma haematobium, Prevalence, PSAC, Caregivers, Risk factors, Zimbabwe

Background

Schistosomiasis is a major public health problem in many tropical and sub-tropical regions [15]. The disease is endemic in 78 countries worldwide where approximately 206.4 million people require preventive chemotherapy, with 92% of them residing in Africa [3]. In 2010, the national survey in Zimbabwe reported an overall prevalence of 22.7% for S. haematobium and S. mansoni infections in school-aged children (SAC) [6]. Although S. haematobium is the most prevalent in the country, the distribution of both species is dependent on the availability and abundance of their intermediate host snails, Bulinus globosus and Biomphalaria pfeifferi, respectively [6, 7]. The presence of suitable intermediate hosts and transmission of schistosomiasis is also dependent on favourable climatic factors with temperature being the main driving factor [4, 8]. Other factors contributing to the distribution of the disease include water contact practice, lack of access to safe water and low socio-economic status [911]. Thus, profiling these factors in endemic communities is vital for improving control programmes towards achieving maximum benefit. Schistosomiasis control in sub-Saharan Africa has been implemented mainly through preventative chemotherapy involving the mass drug administration (MDA) of praziquantel, primarily to SAC [5, 6, 10, 12, 13]. However, the most recent World Health Assembly resolution of 2012 (WHA 65.21) [14] on schistosomiasis elimination advocates for the inclusion of all high-risk groups including preschool-aged children (PSAC) (1–5 years-old) and adults into the MDA campaigns [5, 1523]. While it is acknowledged that most PSAC are too young to engage in water contact activities, there is a plethora of evidence showing that young pre-schoolers are regularly exposed to schistosome infection by their caregivers who take them to fresh water sources or use water from these sources for bathing. The older and more mobile group of PSAC visit water bodies for swimming, washing, bathing and other activities [22, 24]. However, there is a paucity of data on knowledge, perceptions, water contact and sanitary practices of women and the risk factors predisposing their PSAC and themselves to schistosomiasis infection in endemic areas. Thus, it is imperative to elucidate the epidemiological determinants of childhood and maternal schistosomiasis risk and infection.

Although the burden and morbidity, due to schistosomiasis, in women and PSAC has been separately described in Zimbabwe [15, 16, 19], this study aimed to determine the distribution of urogenital schistosomiasis infection in PSAC and their caregivers in Shamva District, the most endemic district in the country [6]. The study also aimed to determine if the caregivers’ water contact practices, knowledge and perceptions are risk factors predisposing them and PSAC to schistosomiasis.

Methods

Study area

The study area has been previously described [15]. The study was conducted in five communities (Mupfure, Chihuri, Nduna, Chakondora and Kaziro) located in Shamva District, Mashonaland Central Province, Zimbabwe (Fig. 1). Shamva District was purposively selected due to the high prevalence (62%) of schistosomiasis among SAC recorded during the 2010 national epidemiological survey [6].

Fig. 1.

Fig. 1

Map showing study area and prevalence of urogenital schistosomiasis for each community. The combined schistosomiasis prevalence for caregivers and children in each community is shown

Most inhabitants of the area are of the Shona ethnic group, mostly Christians. The study communities are located approximately 55 km from Bindura, the nearest town with a provincial hospital. Within the study area, there is one inadequately staffed clinic with two nurses but no doctors. Some communities are as far as 10 km away from the clinic. The study communities are located near one big river (Mupfure), and three small rivers (Nyamaruru, Nyarukunda and Kamoyo) serving as sources of fresh water for most household activities and farming purposes. The area receives high rainfall, averaging 175 mm/month during the rainy season (November–March) but is dry between May and October. Most communities do not have a safe water supply for drinking and only one borehole is located within a 5 km radius. The study communities are heavily involved in vegetable gardening and tobacco farming, which serves as the main source of income for a significant number of families.

Study design

The study was cross-sectional in design and was conducted within a major study investigating host-schistosome interactions: Disease burden in children aged five years and below, mothers and compliance during a one-year schistosomiasis control programme in a district described as highly endemic in Zimbabwe.

Inclusion and exclusion criteria

Figure 2 illustrates how participants were recruited and included into the study. Children aged 5 years and below and their caregivers (17–49 years) were recruited into the study. There were few exceptions in which non-targeted elderly women > 49 years and young adult women below 17 years were included in the study if they were guardians of the PSAC. The PSAC were included in the study if they managed to submit a urine sample to test for urogenital schistosomiasis infection. A total of 426 caregivers and 544 children were eligible for enrolment into the study. The difference in number of caregivers vs PSAC enrolled was the result of some caregivers bringing more than one child aged 5 years and below. Among the 544 eligible children, 9 could not provide a urine sample and so did not participate in the study. All the 426 caregivers responded to the knowledge, perceptions and practices (KPP) questionnaire, of which 325 also managed to submit urine samples for urogenital schistosomiasis diagnosis.

Fig. 2.

Fig. 2

Description of participant recruitment into the study. Children were recruited first and all caregivers of eligible children were included into the study

Sample size

In estimating the sample size of the study population, the 62% schistosomiasis prevalence rate previously reported was used [6]. The assumption that the prevalence of schistosomiasis in SAC is a proxy of the community prevalence was also considered [25]. The required sample size of 363 PSAC and 363 caregivers was calculated using Dobson’s formula as follows:

n=Z2α2pqd2

where Z is the Z-value for the 95% confidence interval, that is alpha = 5% (Z = 1.96), p is the proportion/ prevalence of the outcome to be investigated (p = 0.62), q = 1 − p = 0.38, d is the precision for the given confidence interval expected expressed as a decimal (d = 0.05) and n = 363

The final sample size contained 535 children and 325 caregivers, giving a total of 860 participants.

Sampling procedures

Caregivers and their PSAC were invited to a sampling centre through the community nurse and village health workers. For each community, the study used the Expanded Programme for Immunisation centre (e.g. primary health centre or school) as a sampling centre. Each participant was given a unique identification number. For the caregivers, the same identification number was used on the questionnaire, urine sample and the parasitological results of the participant. For the children, the same identification number was used on the urine sample and parasitological results of the participant. In addition, the child’s study identification number was also captured on the caregiver’s questionnaire.

Questionnaire

To assess the risk factors of urogenital schistosomiasis in the study population, a KPP questionnaire was initially developed in English and translated into the local language (Shona). A separate person blinded to the original English version back-translated the Shona version to English. The validated Shona survey questionnaire was used to collect data from the caregivers. Trained village health workers and nurses administered the questionnaire, which recorded the participants’ demographic characteristics, and knowledge, perceptions and practices related to schistosomiasis infection using both close ended and open ended questions to capture elements of qualitative and quantitative data. Additional information on the knowledge of current and past occurrences of urogenital schistosomiasis, symptoms, prevention methods of infection, water contact practices and risk group perceptions were captured from the caregivers.

Specimen collection for parasitological diagnosis

Individual participants (caregivers and their PSAC) were provided with screw-capped urine containers, for each individual, labelled with their identification number. Urine was collected from children on two consecutive days. For logistical and compliance reasons, only one urine sample was collected from caregivers. Approximately 50 ml of urine was collected from each participant between 10:00 and 14:00 h, a period when peak egg excretion is expected [26]. For the PSAC, their caregivers were directed on how to assist the children in collecting the urine sample. Urine bags (Hollister 7511 U-Bag Urine Specimen Collector, Hollister Inc., Chicago, IL, USA) labelled with the child’s identification number were provided to caregivers with children who could not provide urine samples in screw cap containers. The caregivers were instructed on how to use the urine bags. The collected samples were transported to the field laboratory for processing and analysis within 2 h.

Urine laboratory analysis and microscopic examination

Collected urine samples were first examined macroscopically for visible blood (haematuria). Secondly, a urinary dipstick reagent strip (Spinreact, Girona, Spain) was used for the detection of microhaematuria following the manufacturer’s instructions. The urinalysis reagent strip was dipped into the sample bottle containing urine and immediately removed. The resulting change in colour of the reagent strip was recorded after 1 min and this was compared with the manufacturer’s chart to estimate the amount of blood in the urine sample. The concentration of blood in urine was semi-quantitatively recorded following the manufacturer’s guidelines as: negative (−); light intensity (+); medium intensity (++); and heavy intensity (+++). Blood in urine was considered to indicate S. haematobium infection. Caregivers were requested to indicate if they were menstruating. For all menstruating women, blood in urine was not considered to indicate S. haematobium infection.

Lastly, the urine samples were examined for S. haematobium eggs using the urine filtration technique as described by Mott et al. [27]. In brief, 10 ml of each thoroughly mixed urine sample was syringed through a Nytrel filter (12 µm pore size and 13 mm in diameter). The filter was then placed on the ordinary microscope slide and a drop of 10% Lugol’s iodine was added. The filter membrane was examined under a microscope for S. haematobium eggs. The intensity was expressed as the number of eggs per 10 ml of urine (EP10 ml). Participants were considered infected if at least one egg was detected in any of their urine samples.

Administration of praziquantel to study participants

Following parasitological diagnosis of all urine samples, participants found positive for urogenital schistosomiasis (those with eggs in urine) were given bread and orange juice to eat, after which they were administered a single dose of praziquantel at the recommended dose of 40 mg/kg body weight by the local nurse. For the PSAC, those found positive were given praziquantel crushed and dissolved in orange juice for easy swallowing of the estimated praziquantel dose.

Data analysis

Data were double-entered in Microsoft Excel and exported to STATA v.15.2.0 (Stata Corp, College Station, TX, USA) for analysis. Age was categorized into the following groups: < 1, 1, 2, 3, 4, 5 years for the children, and 15–19, 20–24, 25–29, 30–34, 35–39, 40–44, 45–49, ≥ 50 years for the caregivers. Infection intensity for each infected individual was categorized according to the World Health Organization guidelines (1–49 eggs/10 ml, light intensity; ≥ 50 eggs/10 ml, heavy intensity) [25]. Mann-Whitney test was used to test the difference in Schistosoma egg intensity, whilst association between categorical variables was assessed using a Chi-square test. Continuous variables that were non-normal were summarised using median and interquartile range.

Descriptive analysis of the KPP data was performed and results were reported as frequencies and percentages for all categorical variables. To determine the risk factors of schistosomiasis infection, we performed both univariate and multiple variable logistic regression analysis to identify if S. haematobium infection in either children or caregivers was associated with KPP information. Odds ratios (ORs) and 95% confidence intervals (95% CI) were estimated and reported. A significance level was set at 5%.

Results

Demographic characteristics of participants

In total, 860 participants [535 (62.2%) PSAC, 325 (37.8%) caregivers] were recruited from the five communities as follows: Chakondora, 190 (22.1%); Chihuri, 184 (21.4%); Kaziro, 130 (15.1%); Mupfure, 255 (29.7%); and Nduna, 101 (11.7%) (Table 1). Of the total participants, 569 (66.2%) were female participants (caregivers = 325 and PSAC = 244) while 291 (33.8%) were male PSAC participants. The mean age (SD) of caregivers in the study population was 32.3 (9.0) years. In the PSAC group, the mean (SD) age of the children was 3.0 (1.2) years. There was no significant difference in mean age between males and females in the PSAC group (t(533) = − 1.3037, P = 0.1929).

Table 1.

Demographic characteristics and prevalence of S. haematobium among PSAC and caregivers

Variable No. examined (%) No. infected (prevalence) 95% CI χ2-value P-value
Overall 860 (100) 132 (15.4) 13.0–17.9
Community
 Chakondora 190 (22.1) 16 (8.4) 4.9–13.3 17.375 0.002
 Chihuri 184 (21.4) 42 (22.8) 17.0–29.6
 Kaziro 130 (15.1) 16 (12.3) 7.2–19.2
 Mupfure 255 (29.7) 45 (17.7) 13.2–22.9
 Nduna 101 (11.7) 13 (12.9) 7.0–21.0
Study group
 Caregivers 325 (37.8) 61 (18.7) 14.7–23.4 4.704 0.030
 Children 535 (62.2) 71 (13.3) 10.5–16.4
Gender
 Male 291 (33.8) 36 (12.4) 8.8–16.7 1.946 0.163
 Female 569 (66.2) 96 (16.9) 13.9–20.2
Age categories (years)
 Children 17.203 0.004
  < 1 7 (1.3) 0 (0)
  1 76 (14.2) 4(5.3) 1.5– 12.9
  2 80 (15.0) 10 (12.5) 6.2– 21.8
  3 171 (32.0) 17 (9.9) 5.9–15.4
  4 129 (24.1) 22 (17.1) 11.0–24.7
  5 72 (13.5) 18 (25.0) 15.3–36.6
 Adults 5.546 0.594
  15–19 9 (2.8) 3 (33.3) 7.5–7.0
  20–24 54 (16.6) 15 (27.8) 16.5–41.6
  25–29 65 (20.0) 12 (18.5) 9.9–3.0
  30–34 82 (25.2) 13 (15.9) 8.7–25.6
  35–39 67 (20.6) 10 (14.9) 7.4–25.7
  40–44 27 (8.3) 5 (18.5) 6.3–38.1
  45–49 6 (1.9) 1 (16.7) 0.4–64.1
  ≥ 50 15 (4.6) 2 (13.3) 1.7–40.5

Note: Female includes both female children and adult women

Prevalence of S. haematobium in caregivers and PSAC

The overall prevalence of S. haematobium in our study was 15.4% (95% CI: 13.0–17.9) (Table 1). Schistosoma haematobium infection was significantly higher in caregivers (61; 18.7%) than in PSAC (71; 13.3%) (χ2 = 4.7040, df = 1, P = 0.030). The prevalence of infection was also significantly different among all the study participants age groups (χ2 = 26.4519, df = 13, P = 0.015). Likewise, S. haematobium prevalence was significantly different among communities (χ2 = 17.3750, df = 4, P = 0.002), being most prevalent in Chihuri (22.8%) and least prevalent in Chakondora (8.4%) (Fig. 1, Table 1). However, no difference was observed in urogenital schistosomiasis prevalence after stratification by gender (χ2 = 3.0015, df = 1, P = 0.083). In the PSAC group, S. haematobium prevalence significantly differed among age groups (χ2 = 17.2035, df = 5, P = 0.004). Notably, a prevalence of 0% was recorded in the < 1-year group, while 25% was recorded among those aged 5 years (Table 1).

Schistosoma haematobium infection intensity

A total of 132 S. haematobium-positive participants had a median egg intensity of 5.2 (interquartile range: 2–11.3) eggs per 10 ml of urine. Table 2 describes the infection intensity among participants. The proportion of light infection intensities (93.2%) was significantly higher than heavy infections (6.8%) (Z = 14.0324, df= 1, P ≤ 0.001). This significant difference was also reflected among the communities (χ2 = 10.8532, df = 4, P = 0.028). Caregivers had significantly higher light infection intensities (93.4%) than heavy infections (6.6%) (Z = − 9.5968, P ≤ 0.001). However, no significant difference existed between the caregivers’ infection intensities between the communities (χ2 = 4.2680, df = 4, P = 0.371). The PSAC had significantly higher light intensity infections (93.0%) than heavy infections (7.0%) (Z = − 10.2380, P ≤ 0.001). Similarly, infection intensity in the PSAC was significantly different among communities (χ2 = 12.5339, df = 4, P = 0.014). However, no significant difference was observed when PSAC were classified in relation to the gender (χ2 = 0.1860, df = 1, P = 0.666).

Table 2.

Infection intensity estimates among PSAC and caregivers

Variable Total Caregivers PSAC
No. examined Infection intensity No. examined Infection intensity No. examined Infection intensity
Light
n (%)
Heavy
n (%)
P-value Light
n (%)
Heavy
n (%)
P-value Light
n (%)
Heavy
n (%)
P-value
Total infected 132 123 (93.2) 9 (6.8) < 0.001 61 57 (93.4) 4 (6.6) < 0.001 71 66 (93.0) 5 (7.0) < 0.001
Sex
 Male 36 33 (91.7) 3 (8.3) 0.672 36 33 (91.7) 3 (8.3) 0.666
 Female 96 90 (93.8) 6 (6.3) 61 57 (93.4) 4 (6.6) 35 33 (94.3) 2 (5.7)
Community
 Chakondora 16 16 (100) 0 (0) 0.028 9 9 (100) 0 (0) 0.371 7 7 (100) 0 (0) 0.014
 Chihuri 42 39 (92.9) 3 (7.1) 21 19 (90.5) 2 (9.5) 21 20 (95.2) 1 (4.76)
 Kaziro 16 12 (75.0) 4 (25.0) 12 10 (83.3) 2 (16.7) 4 2 (50.0) 2 (50.0)
 Mupfure 45 43 (95.6) 2 (4.4) 13 13 (100) 0 (0) 32 30 (93.8) 2 (6.3)
 Nduna 13 13 (100) 0 (0) 6 6 (100) 0 (0) 7 7 (100) 0 (0)

Macrohaematuria, microhaematuria and microhaematuria intensity

Macrohaematuria was examined in 834 participants. Overall, macrohaematuria was observed in 14 (1.7%) participants. There was no significant difference between the prevalence of macrohaematuria in caregivers (8; 2.5%) compared to PSAC (6; 1.2%) (χ2 = 1.9775, df = 1, P = 0.160). However, there was a significant difference in the prevalence of macrohaematuria between the communities (χ2 = 18.8894, df = 4, P = 0.001).

Overall, microhaematuria was detected in 10.9% of the 832 participants. There was marginal evidence of difference in the microhaematuria between caregivers (13.5%) and PSAC (9.3%) (χ2 = 3.7039, df = 1, P = 0.054). The prevalence of microhaematuria was also significantly different between communities (χ2 = 13.1950, df = 4, P = 0.010). Microhaematuria intensity was insignificantly higher in caregivers than in PSAC (χ2 = 4.3226, df = 3, P = 0.229) (Table 3).

Table 3.

Prevalence and intensity of microhaematuria and macrohaematuria among participants

Variable Total Caregiver Children P-value
No. examined Prevalence
n (%)
95% CI No. examined Prevalence
n (%)
95% CI No. examined Prevalence
n (%)
95%CI
Macrohaematuria
 Overall 834 14 (1.7) 0.1–2.8 325 8 (2.5) 1.1–4.8 509 6 (1.2) 0.4–2.5 0.160
Community
 Chakondora 183 2 (1.1) 0.1–3.9 52 1 (1.9) 0.0–10.3 131 1 (0.8) 0.0–4.2 0.001
 Chihuri 182 1 (0.6) 0.0–3.0 81 0 (0) 101 1 (1.0) 0.0–5.4
 Kaziro 130 8 (6.2) 2.7–11.8 63 6 (9.5) 3.6–19.6 67 2 (3.0) 0.4–10.4
 Mupfure 248 2 (0.8) 0.0–2.9 86 1 (1.2) 0.0–6.3 162 1 (0.6) 0.0–3.4
 Nduna 91 1 (1.1) 0.0–6.0 43 0 (0) 48 1 (2.1) 0.0–11.1
Microhaematuria
 Overall 832 91 (10.9) 8.9–13.3 325 44 (13.5) 10.0–17.7 507 47 (9.3) 6.9–12.1 0.054
Community
 Chakondora 183 10 (5.5) 2.7–9.8 325 6 (11.5) 4.5–23.4 507 4 (3.1) 0.8–7.6 0.010
 Chihuri 180 27 (15.0) 10.1–21.1 325 12 (14.8) 7.9–24.4 507 15 (15.2) 8.7–23.8
 Kaziro 130 18 (13.9) 8.4–21.0 325 13 (20.6) 11.5–32.7 507 5 (7.5) 2.5–16.6
 Mupfure 248 31 (12.5) 8.7–17.3 325 10 (11.6) 5.7–20.3 507 21 (13.0) 8.2–19.1
 Nduna 91 5 (5.5) 1.8–12.4 325 3 (7.0) 1.5–19.1 507 2 (4.2) 0.5–14.3
Microhaematuria intensity
 + 832 30 (3.6) 2.4–5.1 325 13 (4.0) 2.1–6.7 507 17 (3.4) 2.0–5.3 0.229
 ++ 832 34 (4.1) 2.8–5.7 325 18 (5.5) 3.3–8.6 507 16 (3.2) 1.8–5.1
 +++ 832 27 (3.3) 2.1–4.7 325 13 (4.0) 2.1–6.7 507 14 (2.8) 1.5–4.6

Caregivers’ knowledge of schistosomiasis

Table 4 describes the knowledge of the study population regarding schistosomiasis symptoms, treatment, prevention and control. However, the difference in knowledge of haematuria as a symptom of schistosomiasis infection was not significantly different (χ2 = 0.7634, df = 1, P = 0.382) between the infected (38, 66.7%) and uninfected caregivers (179, 72.5%). All infected caregivers knew that schistosomiasis could be treated and that treatment can be obtained at a health centre. Treatment was considered to prevent and control the disease by 70 (23.0%) women. The difference in knowledge of provision of safe water, sanitation and hygiene (WASH) facilities would also prevent schistosomiasis infection and transmission between the infected and the uninfected caregivers was significant (χ2 = 3.9261, df = 1, P = 0.048).

Table 4.

Association of caregivers’ knowledge regarding schistosomiasis with infection status among themselves and their children

Categorya Childrenb Child’s infection status Caregivers Caregiver’s infection status
Total Infected Uninfected P-value Total Infected Uninfected P-value
Had knowledge of schistosomiasis 502 (93.8) 69 (97.2) 433 (93.3) 0.208 304 (93.5) 57 (18.8) 247 (81.3) 0.973
Mother’s history of infection
 Had infection before 251 (50.0) 41 (59.4) 210 (48.5) 0.092 148 (48.7) 24 (42.1) 124 (50.2) 0.270
Caregivers indicating they are currently infected
 Yes 152 (30.3) 38 (55.1) 114 (26.3) < 0.001* 96 (31.6) 21 (36.8) 75 (30.4) 0.537
 No 177 (35.3) 13 (18.8) 164 (37.9) 102 (33.6) 16 (28.1) 86 (34.8)
 I don’t know 173 (34.5) 18 (26.1) 155 (35.8) 106 (34.9) 20 (35.1) 86 (34.8)
Schistosomiasis symptoms
 Haematuria 364 (72.5) 52 (75.4) 312 (72.1) 0.568 217 (71.4) 38 (66.7) 179 (72.5) 0.382
 Weight loss 132 (26.3) 15 (21.7) 117 (27.0) 0.355 73 (24.0) 12 (21.1) 61 (24.7) 0.562
 General body weakness 64 (12.8) 6 (8.7) 58 (13.4) 0.277 40 (13.2) 10 (17.5) 30 (12.2) 0.277
 Headache 6 (1.2) 1 (1.5) 5 (1.2) 0.834 5 (1.6) 0 (0) 5 (2.0) 0.279
 Nausea 43 (8.6) 9 (13.0) 34 (7.9) 0.152 27 (8.9) 7 (12.3) 20 (8.1) 0.317
 Dysuria 45 (9.0) 7 (10.1) 38 (8.8) 0.712 32 (10.5) 8 (14.0) 24 (9.7) 0.338
 Poor school performance 7 (1.4) 1 (1.5) 6 (1.4) 0.967 5 (1.6) 0 (0) 5 (2.0) 0.279
 Abdominal pain 34 (6.8) 7 (10.1) 27 (6.2) 0.230 24 (7.9) 3 (5.3) 21 (8.5) 0.414
 Genital itchiness in women 12 (2.4) 2 (2.9) 10 (2.3) 0.768 8 (2.6) 2 (3.5) 6 (2.4) 0.650
 Infertility 7 (1.4) 2 (2.9) 5 (1.2) 0.251 8 (2.6) 1 (1.8) 7 (2.8) 0.646
 Recurrent illness 11 (2.2) 2 (2.9) 9 (2.1) 0.666 6 (2.0) 1 (1.8) 5 (2.0) 0.895
 I don’t know 21 (4.2) 3 (4.4) 18 (4.2) 0.941 18 (5.9) 2 (3.5) 16 (6.5) 0.392
Can schistosomiasis be treated? (Yes) 501 (99.8) 69 (100) 432 (99.8) 0.689 303 (99.7) 57 (100) 246 (99.6) 0.630
Knowledge of Health Centre as a place for schistosomiasis treatment 499 (99.4) 68 (98.6) 431 (99.5) 0.323 301 (99.0) 57 (100) 244 (98.8) 0.403
Prevention and controlc
 Treatment using anti-schistosomal medicine 139 (27.7) 18 (26.1) 121 (27.9) 0.749 70 (23.0) 13 (22.8) 57 (23.1) 0.965
 Avoiding contact with unprotected water bodies 220 (43.8) 25 (36.2) 195 (45.0) 0.171 135 (44.4) 27 (47.4) 108 (43.7) 0.618
 Health education 43 (8.6) 10 (14.5) 33 (7.6) 0.059** 32 (10.6) 8 (14.0) 24 (9.8) 0.344
 Provision of WASHd facilities 70 (14.0) 9 (13.0) 61 (14.1) 0.811 54 (17.8) 5 (8.8) 49 (19.9) 0.048*

aFor the variables with a yes or no response, only the number (%) of the yes responses are documented

bChildren were not interviewed but they are described against their caregiver’s responses

cMore than one response was considered

dWater, sanitation and hygiene

*Significance level of 0.05; **Borderline significance of 0.05

Caregivers’ perceptions and practices regarding schistosomiasis

Perceptions and practices of caregivers in relation to schistosomiasis are described in Table 5. Regarding the current national schistosomiasis treatment programme, for those who knew about schistosomiasis, 303 (99.7%) caregivers, including all infected participants, indicated that the programme is important.

Table 5.

Association of caregivers’ perceptions and practices regarding schistosomiasis with infection status among themselves and their children

Categorya Childrenb Child’s infection status Caregivers Caregiver’s infection status
Total Infected Uninfected P-value Total Infected Uninfected P-value
Perceptions
 Is the current national schistosomiasis treatment programme important? (Yes) 501 (99.8) 69 (100) 432 (99.8) 0.689 303 (99.7) 57 (100) 246 (99.6) 0.630
Which group is most likely infected?c
 Children aged ≤ 5 years 242 (48.1) 34 (49.3) 208 (48.0) 0.848 152 (50.0) 21 (36.8) 131 (53.0) 0.028*
 School-aged children 387 (77.1) 50 (72.5) 337 (77.8) 0.325 226 (74.3) 47 (82.5) 179 (72.5) 0.120
 Adult women 97 (19.3) 19 (27.5) 78 (18.0) 0.063 56 (18.4) 9 (15.8) 47 (19.0) 0.570
 Adult men 64 (12.8) 13 (18.8) 51 (11.8) 0.102 39 (12.8) 3 (5.3) 36 (14.6) 0.058**
 Girls 76 (15.1) 12 (17.4) 64 (14.8) 0.574 45 (14.8) 6 (10.5) 39 (15.8) 0.313
 Boys 86 (17.1) 14 (20.3) 72 (16.6) 0.453 49 (16.1) 8 (14.0) 41 (16.6) 0.635
Practices
 Domestic source of water
  Borehole 337 (63.0) 34 (47.9) 303 (65.3) 0.005* 207 (63.7) 32 (52.5) 175 (66.3) 0.043*
  Dam 13 (2.4) 2 (2.8) 11 (2.4) 0.820 6 (1.9) 0 (0) 6 (2.3) 0.235
  River 110 (20.6) 27 (38.0) 83 (17.9) < 0.001* 68 (20.9) 12 (19.7) 56 (21.2) 0.790
  Well 153 (28.6) 24 (33.8) 129 (27.8) 0.297 98 (30.2) 23(37.7) 75 (28.4) 0.154
 Place of doing laundry
  River 395 (73.8) 57 (80.3) 338 (72.8) 0.670 232 (71.4) 42 (68.9) 190 (72.0) 0.518
  Dam 32 (6.0) 2 (2.8) 30 (6.5) 21 (6.5) 4 (6.6) 17 (6.4)
  Garden well 20 (3.7) 2 (2.8) 18 (3.9) 12 (3.7) 1 (1.6) 11 (4.2)
  Borehole 15 (2.8) 2 (2.8) 13 (2.8) 11 (3.4) 4 (6.6) 7 (2.7)
  Well at home 73 (13.6) 8 (11.3) 65 (14.0) 49 (15.1) 10 (16.4) 39 (14.8)
 Laundry time
  Morning 306 (57.2) 39 (54.9) 267 (57.5) 0.204 180 (55.4) 37 (60.7) 143 (54.2) 0.651
  Afternoon 191 (35.7) 30 (42.3) 161 (34.7) 122(37.5) 20 (32.8) 102 (38. 6)
  Late afternoon 38 (7.1) 2(2.8) 36 (7.8) 23 (7.1) 4 (6.6) 19 (7.2)
 Bathing place
  River 199 (37.2) 37 (52.1) 162 (34.9) 0.034* 114 (35.1) 29 (47.5) 85 (32.2) 0.123
  Dam 5 (0.93) 1 (1.4) 4 (0.9) 5 (1.5) 0 (0) 5 (1.9)
  Garden well 7 (1.3) 2 (2.8) 5 (1.1) 6 (1.9) 2 (3.3) 4 (1.5)
  Borehole 18 (3.4) 2 (2.8) 16 (3.5) 11 (3.4) 2 (3.3) 9 (3.4)
  Protected well 306 (57.2) 29 (40.9) 277 (59.7) 189 (58.2) 28 (45.9) 161 (61.0)
 Bathing time
  Morning 28 (5.2) 3 (4.2) 25 (5.4) 0.452 17 (5.2) 2 (3.3) 15 (5.7) 0.174
  Afternoon 110 (20.6) 11 (15.5) 99 (21.3) 73 (22.5) 9 (14.8) 64 (24.2)
  Late afternoon 397 (74.2) 57 (80.3) 340 (73.3) 235 (72.3) 50 (82.0) 185 (70.1)
 Child goes with mother to the river for laundry
  Yes 362 (67.7) 60 (84.5) 302 (65.1) 0.003* 213 (65.5) 42 (68.9) 171 (64.8) 0.478
  No 143 (26.7) 11 (15.5) 132 (28.5) 90 (27.7) 17 (27.9) 73 (27.7)
  Sometimes 30 (5.6) 0 (0) 30 (6.5) 22 (6.8) 2 (3.3) 20 (7.6)
 Where does child play when mother is doing laundry?
  Playing in shallow water 226 (42.2) 41 (57.8) 185 (39.9) 0.016* 150 (46.2) 32 (52.5) 118 (44.8) 0.198
  Playing in a water filled dish outside the river 81 (15.1) 11 (15.5) 70 (15.1) 44 (13.5) 8 (13.1) 36 (13.6)
  Outside the water 168 (31.4) 16 (22.5) 152 (32.8) 92 (28.3) 11 (18.0) 81 (30.7)
  I don’t go with my child to the river or dam 60 (11.2) 3 (4.2) 57 (12.3) 39 (12.0) 10 (16.4) 29 (11.0)
 Child goes with the mother to the river for bathing
  Yes 272 (50.8) 52 (73.2) 220 (47.4) < 0.001* 163 (50.2) 33 (54.1) 130 (49.24) 0.687
  No 211 (39.4) 14 (19.7) 197 (42.5) 133 (40.9) 24 (39.3) 109 (41.3)
  Sometimes 52 (9.7) 5 (7.0) 47 (10.1) 29 (8.9) 4 (6.7) 25 (9.5)
 Where does child play when mother is bathing?
  Playing in water/bathing also 190 (35.5) 34 (47.9) 156 (33.6) 0.018* 120 (36.9) 29 (47.5) 91 (34.5) 0.100
  Outside the water 123 (23.0) 18 (25.4) 105 (22.6) 79 (24.3) 15 (24.6) 64 (24.2)
  Playing in a water filled dish outside the river 222 (41.5) 19 (26.8) 203 (43.8) 126 (38.8) 17 (27.9) 109 (41.3)
 The usual source of water for bathing the child
  River 175 (32.7) 41 (57.8) 134 (28.9) < 0.001* 110 (33.9) 21 (34.4) 89 (33.7) 0.698
  Dam 6 (1.1) 0 (0) 6 (1.3) 6 (1.9) 0 (0) 6 (2.3)
  Well 56 (10.5) 10 (14.1) 46 (9.9) 35 (10.8) 7 (11.5) 28 (10.6)
  Protected well/borehole/tap 298 (55.7) 20 (28.2) 278 (59.9) 174 (53.5) 33 (54.1) 141 (53.4)
 Do you boil water for bathing the child?
  Yes 373 (69.7) 45 (63.4) 328 (70.7) < 0.001* 216 (66.5) 40 (65.6) 176 (66.7) 0.176
  No 34 (6.4) 12 (16.9) 22 (4.7) 25 (7.7) 8 (13.1) 17 (6.4)
  Sometimes 128 (23.9) 14 (19.7) 114 (24.6) 84 (25.9) 13 (21.3) 71 (26.9)
 Whether child aged ≤ 5 years assist in watering the garden
  Yes 136 (25.4) 31 (43.7) 105 (22.6) < 0.001* 84 (25.9) 19 (31.2) 65 (24.6) 0.566
  No 377 (70.5) 33 (46.5) 344 (744) 228 (70.2) 40 (65.6) 188 (71.2)
  Sometimes 22 (4.1) 7 (9.9) 15 (3.2) 13 (4.0) 2 (3.3) 11 (4.2)
 Presence of a toilet at home 426 (79.6) 59 (83.1) 367 (79.1) 0.435 260 (80.0) 49 (80.3) 211 (79.9) 0.943
 Those using the toilet 454 (84.9) 66 (93.0) 388 (83.6) 0.041* 278 (85.5) 55 (90.2) 223 (84.5) 0.254
 Source of drinking water
  River 40 (7.5) 11 (15.5) 29 (6.3) < 0.001* 19 (5.9) 4 (6.6) 15 (5.7) 0.228
  Protected well at home 127 (23.7) 14 (19.7) 113 (24.4) 86 (26.5) 19 (31.2) 67 (25.4)
  Borehole 337 (63.0) 36 (50.7) 301 (64.9) 202 (62.2) 32 (52.5) 170 (64.4)
  Garden well 31 (5.8) 10 (14.1) 21 (4.5) 18 (5.5) 6(9.8) 12 (4.6)

aFor the variables with a yes or no response, only the number (%) of the yes response are documented

bChildren were not interviewed but they are described against their caregiver’s responses

cMore than one response was considered

*Significance level of 0.05; **Borderline significance of 0.05

While 207 (63.7%) caregivers used borehole water for domestic purposes, its use was significantly higher in the uninfected caregivers (175, 66.3%) compared to those infected (32, 52.5%) (χ2 = 4.0977, df = 1, P = 0.043). Meanwhile, the use of river water for domestic purposes was significantly higher (χ2 = 15.2925, df = 1, P ≤ 0.001) in caregivers of infected children (27, 38.0%) compared to those of uninfected children (83, 17.9%). While 37 (52.1%) of the infected children’s caregivers used river water for bathing, the use of different bathing water sources among the caregivers of infected and uninfected children was significantly different (χ2 = 10.4170, df = 4, P = 0.034). Meanwhile, 41 (57.8%) of the infected children’s caregivers reported that they usually bath their children using river water and the difference in infection among children with varying sources of water for bathing was significantly different (χ2 = 28.7692, df = 3, P ≤ 0.001). For caregivers who took their children to the river for bathing, infection was significantly different (χ2 = 8.0110, df = 2, P = 0.018) among children who played or bathed in river water (34, 47.9%), children who played in a water-filled basin (19, 26.8%) and played outside of the water 18 (25.4%). There was a significantly higher number of infected children (60, 84%) for caregivers who took their children to the river for laundry activities compared to those who did not (11, 15.5%) (χ2 = 11.8896, df = 2, P = 0.003). Consequently, the number of children who were allowed to play in shallow water when the caregivers were performing laundry activities was significantly different between the infected and uninfected category (χ2 = 10.2804, df = 3, P = 0.016).

Association of knowledge, perception and practices of caregivers with urogenital schistosomiasis infection

Table 6 describes the univariate and multivariate logistic regression analysis for the association of knowledge, perception and practices of caregivers with their urogenital schistosomiasis infection.

Table 6.

Association of knowledge, perception and practices of caregivers with their schistosomiasis infection

Variable Response Univariate analysis Multivariate analysis
OR 95% CI P-value Adj OR 95% CI P-value
Perceptions
 School children are the high-risk group Yes 1
No 0.16 0.3–1.2 0.123 0.4 0.2–0.9 0.025*
 Adult men are the high-risk group Yes 1 1
No 3.1 0.9–10.4 0.070 5.2 1.2–21.9 0.024*
Practices
 Those who use borehole water for domestic purposes Yes 1 1
No 1.8 1.0–3.1 0.045* 2.2 1.1–4.3 0.020*
 Source of water for bathing Protected well 1 1
River 2.0 1.1–3.5 0.023* 3.0 1.4–6.4 0.004*
Garden well 2.9 0.5–16.4 0.235 6.5 0.8–56.3 0.088
Borehole 1.3 0.3–6.2 0.762 0.9 0.1–10.0 0.941
 Time of bathing Afternoon 1 1
Morning 0.9 0.2–4.8 0.949 0.9 0.1–6.9 0.934
Late afternoon 1.9 0.9–4.1 0.094 2.4 1.0–5.7 0.055**
 Use of a toilet for excreta disposal Yes 1 1
No 0.6 0.2–1.5 0.259 0.2 0.1–0.9 0.037*

Notes: Reference group is marked as OR or Adj OR = 1. Univariate and multivariate logistic regression analysis of S. haematobium infection in caregivers in relation to sources of water for domestic use, sources of water for laundry, bathing and timing of bathing. In addition, the association of S. haematobium infection with toilet use and perceptions is also presented

*Significance association of 0.05; **Borderline significance of 0.05

Abbreviations: OR, odds ratio; 95% CI, 95% confidence interval; Adj OR, adjusted odds ratio

Among the caregivers, the univariate analysis showed that the risk of acquiring schistosomiasis was associated with the source of water that was being used for domestic purposes (OR: 1.8, 95% CI: 1.0–3.1) and bathing in river water (OR: 2.0, 95% CI: 1.1–3.5) only. After controlling for possible confounders, the multivariate logistic regression analysis showed that the risk of infection was high for caregivers who did not use borehole water for domestic purposes (AOR: 2.2, 95% CI: 1.1–4.3) compared to those who did. The risk was also high for caregivers using river water for bathing (AOR: 3.0, 95% CI: 1.4–6.4) compared to those who use protected well water. Caregivers who did not believe adult men are a high-risk group were at high odds of being infected. Meanwhile, caregivers who did not believe SAC are a high-risk group were 60% less likely to be infected (AOR: 0.4, 95% CI: 0.2–0.9) compared to those who believed SAC are a high-risk group.

Association of knowledge, perception and practices of caregivers with schistosomiasis infection in PSAC

Table 7 describes the univariate and multivariate logistic regression analysis for association of knowledge, perception, and practices of caregivers with their PSAC’s urogenital schistosomiasis infections.

Table 7.

Association of knowledge, perception and practices of caregivers with PSAC’s schistosomiasis infection

Variable Response Univariate analysis Multivariate analysis
OR 95% CI P-value Adj OR 95% CI P-value
Caregiver’s infection status Not infected 1 1
Infected 3.9 1.9–7.7 < 0.001 3.9 1.7–8.6 0.001
Knowledge
 Caregiver indicates they are currently infected No 1
Yes 4.2 2.1–8.2 < 0.001
I don’t know 1.5 0.7–3.1 0.316
Perceptions
 Which group is most likely infected School-aged children
Yes 1 1
No 1.3 0.8–2.4 0.326 2.6 1.1–5.9 0.022
Adult women
Yes 1
No 0.6 0.3–1.0 0.065
Practices
 Source of water for domestic purpose Borehole
Yes 1
No 2.0 1.2–3.4 0.005
 Source of water for bathing Protected well 1
River 2.2 1.3–3.7 0.003
Dam 2.4 0.3–22.1 0.443
Garden well 3.8 0.7–20.6 0.119
Borehole 1.2 0.3–5.5 0.819
 Is the toilet used? Yes 1 1
No 0.4 0.2–1.0 0.048 0.1 0.0–0.5 0.009

Notes: Reference group is marked as OR or Adj OR = 1. Univariate and multivariate logistic regression analysis of S. haematobium infection in PSAC in relation to sources of domestic water, gardening and bathing practices. In addition, the association of S. haematobium infection with toilet use and knowledge of current infection status by the caregiver is also presented

*Significance association of 0.05; **Borderline significance of 0.05

Abbreviations: OR, odds ratio; 95% CI, 95% confidence interval; Adj OR, adjusted odds ratio

Univariate analysis showed that knowledge of caregiver’s current infection status, use of borehole and river water for domestic purposes, use of river water by the caregiver for bathing, allowing the child to play in water when the caregiver is bathing in the river, and bathing the child in river water were all risk factors for schistosomiasis infection. The perceptions that SAC and adult women are high-risk groups for schistosomiasis were not significant with the univariate analysis. Multivariate analysis showed that the odds of being infected was higher for PSAC of caregivers who had schistosomiasis infection (AOR: 3.9, 95% CI: 1.7–8.6) and whose caregivers believed that SAC are a high-risk group.

Discussion

The present study demonstrates that urogenital schistosomiasis is a significant public health problem in caregivers and their PSAC in Shamva District. This adds to the growing evidence regionally [18, 22, 28] on schistosomiasis epidemiology in PSAC and their caregivers and underlines the need to include them in current schistosomiasis treatment programmes. Moreover, the study has contributed to the scarce data demonstrating the KPP of caregivers as risk factors for schistosomiasis infection for themselves and their PSAC.

The difference in knowledge of disease symptoms was generally not significant between infected and uninfected caregivers in the area. Overall, the caregivers generally had a low knowledge of schistosomiasis prevention and control, which will enable sustained infection and transmission in such high-risk communities.

Women did not perceive themselves or their PSAC to be high-risk groups. This results in exposing PSAC, unknowingly, to infection through water contact activities such as allowing them to play or perform activities in the unprotected water while the caregiver is bathing or washing clothes. While most of the caregivers reported the use of toilets for excreta disposal, the few individuals who are infected and are practicing indiscriminate disposal of excreta puts the communities at risk of infection. Moreover, indiscriminate excreta disposal coupled with risky water contact activities reported here, such as bathing in the river or unprotected water sources, highly predispose individuals to schistosomiasis infection. Midzi et al. [29] had earlier reported indiscriminate disposal of excreta and poor water contact practices of SAC from endemic communities in Zimbabwe. Profiling the associations of such practices within an area assists in explaining spatial heterogeneities of disease prevalence [11, 12], in addition to identifying areas needing health education for behavioural change.

While overall disease prevalence was significantly different between caregivers and PSAC, it was higher in caregivers (18.8%) compared to the PSAC (13.3%), substantiating that schistosomiasis infection is a function of duration of exposure [30]. Caregivers have had or have more water contact exposure, thus are likely to have a higher prevalence compared to PSAC. These findings are similar to observations made in Zanzibar [28].

Regarding PSAC, the highest urogenital schistosomiasis prevalence was in the 5-year age group with no infections found in all the children less than one year old and only four (5.3%) children out of the 72 children aged one year were infected. These results corroborated findings reported in Nigeria [31], demonstrating an increase in prevalence of urogenital schistosomiasis infection with the age of the children. As the children grow, their independence also increases resulting in more repeated exposures to infections as they repeatedly play in open and often infective water sources. Limited safe water sources and lack of knowledge on prevention and control of the disease result in a high reliance on unprotected water sources in the study area. Thus, the observed early infections among PSAC less than three years of age will be due to early exposure to contaminated water bodies when they accompany their mothers for different water contact activities, as reported in other settings [18, 22, 28]. This early exposure is regardless of gender as S. haematobium infection was not significantly different between male and female PSAC.

Among all the communities, heavy intensity infections were low, but it could not be clarified why they were highest in Kaziro even though this area had a relatively low prevalence of infection. Identifying, targeting and profiling such individuals with high infection intensities is essential to understanding disease transmission characteristics for maximising control interventions [12]. Moreover, if left unattended, these heavy infections might result in poor growth and cognition in these children [32, 33] and also the development of female and male genital schistosomiasis with added pathological consequences [20].

In this study, the number of recruited caregivers was lower than the PSAC. While some caregivers had more than one PSAC under their care, some caregivers also sent their child along with their neighbour who also brought their own child or children to the urine collection point. Some caregivers ended up bringing three or more PSAC for screening. In the same context, PSAC might be exposed to infection while they are under the care of alternative carers or relatives who might also take them to the unprotected water bodies while performing their water contact activities. This partly explains why some caregivers were not infected yet their children were infected although age related acquired resistance to infection could not be ruled out [34].

The present prevalence recorded in Madziwa, Shamva District among the PSAC (13.3%) is lower than the one recorded in Murewa District, northeast Zimbabwe (~ 20%) in the same age group [16]. However, both Murewa and Shamva districts, according to the WHO classification [6], are high transmission areas having a prevalence of infection greater than 50% [25]. The difference in prevalence may be due to different socio-demographic factors, behavioural practices among the caregivers of the PSAC, in addition to difference in availability of water and sanitation facilities in these two districts; however, more studies are needed to identify the cause of these differences.

The prevalence of infection in caregivers recorded during this study (18.7%) is lower than the one previously recorded in the same area by Ndhlovu et al. [19] in 2007 (29% and above). However, as opposed to the previous study which was inclusive of all women aged 15–49 years in the area, our study only focused on caregivers of PSAC, possibly resulting in an underestimation of the true infection prevalence. Nevertheless, the schistosomiasis prevalence observed provides a starting point for considering large-scale screening of the adult populations so that appropriate intervention strategies can be implemented.

Conclusions

According to the WHO schistosomiasis classification, women and PSAC in Madziwa area belong to the moderate risk category and mass chemotherapy once every two years is recommended to avert the associated morbidity for these specific age groups [35]. Knowledge, perceptions and water contact practices of caregivers are risk factors for schistosomiasis infection in caregivers and their PSAC. Thus, adult women in endemic communities should be included in the design, implementation and evaluation of schistosomiasis control programmes in view of their important role as caregivers, their educational role in raising the awareness of the risk of schistosomiasis infection in their children and as main house hold users of water from non-safe sources.

Acknowledgements

We are grateful to the women and children who participated in the study. Special thanks to the Madziwa community leaders, the village heads and the village health workers for their assistance in mobilization of the community. We are grateful to nurses in the local health facilities and village health workers from the community under study for their assistance in data collection and treatment.

Abbreviations

KPP

knowledge, perceptions and practices

PSAC

preschool-aged children

SAC

school-aged children

WASH

water, sanitation and hygiene

WHA

World Health Assembly

WHO

World Health Organization

Authors’ contributions

MJMM and NM conceived the study. MJMM, NM and CT undertook fieldwork. MJMM, NM and CT obtained ethical clearance. MJMM, ZMZ, NM and AK performed data input and analysis. MJMM, ZMZ, BW, XZ, NC and NM wrote the initial draft of the manuscript. All authors read and approved the final manuscript.

Funding

This study was partly funded by the Thrasher Research Fund (12440).

Availability of data and materials

The data supporting the conclusions of this article are included within the article. The datasets analysed during the present study are available from the corresponding author upon reasonable request.

Ethics approval and consent to participate

Prior to the commencement of the study, approval was obtained from the community leaders, provincial and district directorate of the Ministry of Health and Child Care in the area. Ethical clearance of the study was provided by the Joint Research Ethics Committee (JREC) for the University of Zimbabwe, College Of Health Sciences and the Parirenyatwa Group of Hospitals (JREC/251/16). Further approval was provided by the National Ethical Review Board, the Medical Research Council of Zimbabwe (MRCZ) (MRCZ/A/2149). Visits were made to the various communities in the area, engaging the village heads and village health workers in the communities. The parents were sensitized about the nature of the study and study objectives in local language (Shona). Written informed consent in the local language was obtained from caregivers for both their enrolment and enrolment of their children into the study. Participation was entirely voluntary and only participants with signed informed consent forms were enrolled into the study.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Footnotes

Publisher's Note

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Contributor Information

Masceline Jenipher Mutsaka-Makuvaza, Email: mascelinejeni@gmail.com.

Zvifadzo Matsena-Zingoni, Email: zmatsena28@gmail.com.

Agnes Katsidzira, Email: agnes.katsidzira@gmail.com.

Cremance Tshuma, Email: tshuma.cremance@gmail.com.

Nyasha Chin’ombe, Email: nyasha.chinombe@gmail.com.

Xiao-Nong Zhou, Email: zhouxn1@chinacdc.cn.

Bonnie Webster, Email: b.webster@nhm.ac.uk.

Nicholas Midzi, Email: midzinicholas@gmail.com.

References

  • 1.Gryseels B, Polman K, Clerinx J, Kestens L. Human schistosomiasis. Lancet. 2006;368:1106–1118. doi: 10.1016/S0140-6736(06)69440-3. [DOI] [PubMed] [Google Scholar]
  • 2.Steinmann P, Keiser J, Bos R, Tanner M, Utzinger J. Schistosomiasis and water resources development: systematic review, meta-analysis, and estimates of people at risk. Lancet Infect Dis. 2006;6:4114–4125. doi: 10.1016/S1473-3099(06)70521-7. [DOI] [PubMed] [Google Scholar]
  • 3.World Health Organization. Schistosomiasis; 2018. http://www.who.int/news-room/fact-sheets/detail/schistosomiasis. Accessed 07 June 2018.
  • 4.Pedersen UB, Stendel M, Midzi N, Mduluza T, Soko W, Stensgaard AS, et al. Modelling climate change impact on the spatial distribution of fresh water snails hosting trematodes in Zimbabwe. Parasit Vectors. 2014;7:536. doi: 10.1186/s13071-014-0536-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5.WHO. Schistosomiasis: progress report 2001–2011, strategic plan 2012–2020; 2013. http://apps.who.int/iris/bitstream/10665/78074/1/9789241503174_eng.pdf. Accessed 28 Aug 2017.
  • 6.Midzi N, Mduluza T, Chimbari MJ, Tshuma C, Charimari L, Mhlanga G, et al. Distribution of schistosomiasis and soil-transmitted helminthiasis in Zimbabwe: towards a national plan of action for control and elimination. PLoS Negl Trop Dis. 2014;8:e3014. doi: 10.1371/journal.pntd.0003014. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Woolhouse ME, Chandiwana SK. Spatial and temporal heterogeneity in the population dynamics of Bulinus globosus and Biomphalaria pfeifferi and in the epidemiology of their infection with schistosomes. Parasitology. 1989;98:21–34. doi: 10.1017/S0031182000059655. [DOI] [PubMed] [Google Scholar]
  • 8.Shiff CJ, Evans A, Yiannakis C, Eardley M. Seasonal influence on the production of Schistosoma haematobium and S. mansoni cercariae in Rhodesia. Int J Parasitol. 1975;5:119–123. doi: 10.1016/0020-7519(75)90109-5. [DOI] [PubMed] [Google Scholar]
  • 9.Roy E, Hasan KZ, Haque R, Haque AKMF, Siddique A, Sack RB. Patterns and risk factors for helminthiasis in rural children aged under 2 in Bangladesh. S Afr J Child Heal. 2011;5:78–84. [Google Scholar]
  • 10.Hotez PJ, Bund DAP, Beegle K, Brooker S, Drake L, de Silva N, et al. et al. Helminth infections: Soil-transmitted helminth infections and schistosomiasis. In: Jamison DT, Breman JG, Measham AR, Alleyne G, Claeson M, Evans DB, et al.et al., editors. Disease control priorities in developing countries. 2. Washington (DC): World Bank; 2006. [PubMed] [Google Scholar]
  • 11.Kloos H, Fulford AJ, Butterworth AE, Sturrock RF, Ouma JH, Kariuki HC, et al. Spatial patterns of human water contact and Schistosoma mansoni transmission and infection in four rural areas in Machakos District, Kenya. Soc Sci Med. 1997;44:949–968. doi: 10.1016/S0277-9536(96)00218-3. [DOI] [PubMed] [Google Scholar]
  • 12.Chadeka EA, Nagi S, Sunahara T, Cheruiyot NB, Bahati F, Ozeki Y, et al. Spatial distribution and risk factors of Schistosoma haematobium and hookworm infections among schoolchildren in Kwale, Kenya. PLoS Negl Trop Dis. 2017;11:e0005872. doi: 10.1371/journal.pntd.0005872. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Montresor A. Helminth control in school-age children. A guide for managers of control programmes. 2. Geneva: WHO; 2011. [Google Scholar]
  • 14.Sixty Fifth World Health Assembly. Elimination of Schistosomiasis; 2012. www.who.int/neglected_diseases/media/centre/WHA_65.21_Eng.pdf. Accessed 30 July 2017.
  • 15.Mutsaka-Makuvaza MJ, Matsena-Zingoni Z, Tshuma C, Ray S, Zhou XN, Webster B, et al. Re-infection of urogenital schistosomiasis in pre-school children in a highly endemic district in northern Zimbabwe: compliance assessment in a 12 months longitudinal study. Infect Dis Poverty. 2018;7:102. doi: 10.1186/s40249-018-0483-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Wami WM, Nausch N, Bauer K, Midzi N, Gwisai R, Simmonds P, et al. Comparing parasitological vs serological determination of Schistosoma haematobium infection prevalence in preschool and primary school-aged children: implications for control programmes. Parasitology. 2014;141:1962–1970. doi: 10.1017/S0031182014000213. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Navaratnam AMD, Sousa-Figueiredo JC, Stothard JR, Kabatereine NB, Fenwick A, Mutumba-Nakalembe MJ. Efficacy of praziquantel syrup versus crushed praziquantel tablets in the treatment of intestinal schistosomiasis in Ugandan preschool children, with observation on compliance and safety. Trans R Soc Trop Med Hyg. 2012;106:400–407. doi: 10.1016/j.trstmh.2012.03.013. [DOI] [PubMed] [Google Scholar]
  • 18.Betson M, Sousa-Figueiredo JC, Rowell C, Kabatereine NB, Stothard JR. Intestinal schistosomiasis in mothers and young children in Uganda: investigation of field-applicable markers of bowel morbidity. Am J Trop Med Hyg. 2010;83:1048–1055. doi: 10.4269/ajtmh.2010.10-0307. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Ndhlovu PD, Mduluza T, Kjetland EF, Midzi N, Nyanga L, Gundersen SG, et al. Prevalence of urinary schistosomiasis and HIV in females living in a rural community of Zimbabwe: does age matter? Trans R Soc Trop Med Hyg. 2007;101:433–438. doi: 10.1016/j.trstmh.2006.08.008. [DOI] [PubMed] [Google Scholar]
  • 20.Kjetland EF, Kurewa EN, Mduluza T, Midzi N, Gomo E, Friis H, et al. The first community-based report on the effect of genital Schistosoma haematobium infection on female fertility. Fertil Steril. 2010;94:1551–1553. doi: 10.1016/j.fertnstert.2009.12.050. [DOI] [PubMed] [Google Scholar]
  • 21.Stothard JR, Sousa-Figueiredo JC, Betson M, Seto EYW, Kabatereine NB. Investigating the spatial micro-epidemiology of diseases within a point-prevalence sample: a field applicable method for rapid mapping of households using low-cost GPS-dataloggers. Trans R Soc Trop Med Hyg. 2011;105:500–506. doi: 10.1016/j.trstmh.2011.05.007. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Seto EYW, Sousa-Figueiredo JC, Betson M, Byalero C, Kabatereine NB, Stothard JR. Patterns of intestinal schistosomiasis among mothers and young children from Lake Albert, Uganda: water contact and social networks inferred from wearable global positioning system dataloggers. Geospat Health. 2012;7:1–13. doi: 10.4081/gh.2012.99. [DOI] [PubMed] [Google Scholar]
  • 23.King CH. The evolving schistosomiasis agenda 2007–2017 - Why we are moving beyond morbidity control toward elimination of transmission. PLoS Negl Trop Dis. 2017;11:e0005517. doi: 10.1371/journal.pntd.0005517. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Ekpo UF, Oluwole AS, Abe EM, Etta HE, Olamiju F, Mafiana CF. Schistosomiasis in infants and pre-school-aged children in sub-Saharan Africa: implication for control. Parasitology. 2012;139:835–841. doi: 10.1017/S0031182012000029. [DOI] [PubMed] [Google Scholar]
  • 25.World Health Organization Expert Committee on the Control of Schistosomiasis Prevention and control of schistosomiasis and soil-transmitted helminthiasis: report of a WHO expert committee. World Health Organ Tech Rep Ser. 2002;912:1–57. [PubMed] [Google Scholar]
  • 26.Doehring E, Feldmeier H, Daffalla AA. Day-to-day variation and circadian rhythm of egg excretion in urinary schistosomiasis in the Sudan. Ann Trop Med Parasitol. 1983;77:587–594. doi: 10.1080/00034983.1983.11811757. [DOI] [PubMed] [Google Scholar]
  • 27.Mott KE, Baltes R, Bambagha J, Baldassini B. Field studies of a reusable polyamide filter for detection of Schistosoma haematobium eggs by urine filtration. Trop Med Parasitol. 1982;33:227–228. [PubMed] [Google Scholar]
  • 28.Sousa-Figueiredo JC, Basáñez M-G, Mgeni AF, Khamis IS, Rollinson D, Stothard JR. A parasitological survey, in rural Zanzibar, of pre-school children and their mothers for urinary schistosomiasis, soil-transmitted helminthiases and malaria, with observations on the prevalence of anaemia. Ann Trop Med Parasitol. 2008;102:679–692. doi: 10.1179/136485908X337607. [DOI] [PubMed] [Google Scholar]
  • 29.Midzi N, Mtapuzi-Zinyowera S, Mapingure MP, Paul NH, Hlerema G, Mutsaka MJ, et al. Knowledge attitudes and practices of grade three primary schoolchildren in relation to schistosomiasis, soil transmitted helminthiasis and malaria in Zimbabwe. BMC Infect Dis. 2011;11:169. doi: 10.1186/1471-2334-11-169. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.Dalton PR, Pole D. Water-contact patterns in relation to Schistosoma haematobium infection. Bull World Health Organ. 1978;56:417–426. [PMC free article] [PubMed] [Google Scholar]
  • 31.Mafiana CF, Ekpo UF, Ojo DA. Urinary schistosomiasis in preschool children in settlements around Oyan Reservoir in Ogun State, Nigeria: implications for control. Trop Med Int Health. 2003;8:78–82. doi: 10.1046/j.1365-3156.2003.00988.x. [DOI] [PubMed] [Google Scholar]
  • 32.Osakunor DNM, Mduluza T, Midzi N, Chase-Topping M, Mutsaka-Makuvaza MJ, Chimponda T, et al. Dynamics of paediatric urogenital schistosome infection, morbidity and treatment: a longitudinal study among preschool children in Zimbabwe. BMJ Glob Health. 2018;3:e000661. doi: 10.1136/bmjgh-2017-000661. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 33.Nokes C, McGarvey ST, Shiue L, Wu G, Wu H, Bundy DA, et al. Evidence for an improvement in cognitive function following treatment of Schistosoma japonicum infection in Chinese primary schoolchildren. Am J Trop Med Hyg. 1999;60:556–565. doi: 10.4269/ajtmh.1999.60.556. [DOI] [PubMed] [Google Scholar]
  • 34.Etard JF, Audibert M, Dabo A. Age-acquired resistance and predisposition to infection with Schistosoma haematobium after treatment with praziquantel in Mali. Am J Trop Med Hyg. 1995;52:549–558. doi: 10.4269/ajtmh.1995.52.549. [DOI] [PubMed] [Google Scholar]
  • 35.Montresor A, Crompton DWT, Hall A, Bundy DAP, Savioli L. Guidelines for the evaluation of soil-transmitted helminthiasis and schistosomiasis at community level. A guide for managers of control programmes. Geneva: WHO; 1998. [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

The data supporting the conclusions of this article are included within the article. The datasets analysed during the present study are available from the corresponding author upon reasonable request.


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