Journal of Tropical Medicine
Volume 2020 (2020), Article ID 8850840, 18 pages
https://doi.org/10.1155/2020/8850840

Review Article

Prevalence of Schistosoma mansoni and S. haematobium in Snail Intermediate Hosts in Africa: A Systematic Review and Meta-analysis

Tamirat Hailegebriel, Endalkachew Nibret, and Abaineh Munshea

Department of Biology, College of Science, Bahir Dar University, Bahir Dar, Ethiopia

Correspondence should be addressed to Tamirat Hailegebriel; tamiratbdu@gmail.com

Received 28 July 2020; Revised 26 August 2020; Accepted 28 August 2020; Published 7 September 2020

Academic Editor: Pedro P. Chieffi

Copyright © 2020 Tamirat Hailegebriel et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

Background. Schistosomiasis is caused by Schistosoma mansoni and S. haematobium in Africa. These schistosome parasites use freshwater snail intermediate hosts to complete their lifecycle. Varied prevalence rates of these parasites in the snail intermediate hosts were reported from several African countries, but there were no summarized data for policymakers. Therefore, this study was aimed to systematically summarize the prevalence and geographical distribution of S. mansoni and S. haematobium among freshwater snails in Africa. Methods. Literature search was carried out from PubMed, Science Direct, and Scopus which reported the prevalence of S. mansoni and S. haematobium among freshwater snails in Africa. The pooled prevalence was determined using a random-effect model, while heterogeneities between studies were evaluated by I² test. The meta-analyses were conducted using Stata software, metan command. Results. A total of 273,643 snails were examined for the presence of S. mansoni and S. haematobium cercaria in the eligible studies. The pooled prevalence of schistosome cercaria among freshwater snails was 5.5% (95% CI: 4.9–6.1%). The pooled prevalence of S. mansoni and S. haematobium cercaria was 5.6% (95% CI: 4.9–6.3%) and 5.2% (95% CI: 4.6–5.7%), respectively. The highest pooled prevalence was observed from Nigeria (19.0%; 95% CI: 12.7–25.3%), while the lowest prevalence was reported from Chad (0.05%; 95% CI: 0.03–0.13). Higher prevalence of schistosome cercaria was observed from Bulinus globosus (12.3%; 95% CI: 6.2–18.3%) followed by Biomphalaria sudanica (6.7%; 95% CI: 4.5–9.0%) and Biomphalaria pfeifferi (5.1%; 95% CI: 4.1–6.2%). The pooled prevalence of schistosome cercaria obtained using PCR was 26.7% in contrast to 4.5% obtained by shedding cercariae. Conclusion. This study revealed that nearly 6% of freshwater snails in Africa were infected by either S. haematobium or S. mansoni. The high prevalence of schistosomes among freshwater snails highlights the importance of appropriate snail control strategies in Africa.

1. Introduction

Schistosomiasis is one of the neglected tropical diseases (NTD) endemic in 78 countries and infects more than 229 million peoples in tropical and subtropical regions [1]. More than 90% of these cases are concentrated in Africa [2, 3]. The burden of the disease is even more severe in sub-Saharan Africa. Poor environmental sanitation and suitability of the climate conditions for snail intermediate host contribute to the high endemicity of the region. Schistosomiasis ranks second next to malaria from parasitic infection in terms of socioeconomic and health impact in tropics [4].

Human schistosomiasis is caused by Schistosoma mansoni, S. haematobium, S. japonicum, S. intercalatum, S. mekongi, S. malayensis, and S. guineensis [5–7]. Among these species, S. mansoni, S. haematobium, and S. japonicum are the major causes of human schistosomiasis globally [8]. Schistosoma mansoni and S. haematobium are widely distributed and the dominant cause of human schistosomiasis in Africa [5]. The endemicity of the disease in the region is linked with the availability of freshwater snail intermediate hosts.

About 350 species of freshwater snails are known to be medically or veterinary important [9]. Among these diverse snails, Biomphalaria, Bulinus, and Oncomelania snails [4] are the dominant snail genera that are involved in the transmission of human schistosomiasis. The Biomphalaria genus consists of B. pfeifferi, B. glabrata, B. sudanica, B. straminea, B. tenagophila, B. alexandarina, and B. choanomphala [10]. Biomphalaria snails serve as the intermediate host for S. mansoni, which is responsible for intestinal and hepatic schistosomiasis. Biomphalaria pfeifferi is the most common and widely distributed snail intermediate host for S. mansoni in Africa.

Bulinus consists of 37 recognized species, which is grouped mainly into four species groups, namely, Bulinus africanus, B. forskalii, B. truncates/tropicus, and B. reticulatus [10, 11]. Bulinus snails serve as intermediate hosts for S. haematobium, which is responsible for urinary schistosomiasis. Oncomelania snails consist of only a few species mainly reported from Asia. The most common snail intermediate host for S. japonicum is Oncomelania hupensis, which is found in China, the Philippines, Indonesia, and also Japan [12].

The prevalence of human schistosomiasis is varied greatly in African countries depending on the level of environmental sanitation and the suitability of the area for the snail intermediate hosts, as well as the type of snail in the area. Similarly, the prevalence of schistosomes cercaria in snail intermediate hosts is varied in different locations within the same country and also from country to country in Africa. Several epidemiological studies are available on the types and prevalence of human infecting schistosomes among snail intermediate hosts in Africa. However, up to this time, there has not been any single estimate of the prevalence of S. mansoni and S. haematobium in snail intermediate hosts in Africa that could be used by African policymakers and international organizations working on the prevention and control of schistosomiasis in the continent. Therefore, this study aimed to provide summarized data on the prevalence and geographical variations of S. mansoni and S. haematobium cercaria among freshwater snails in Africa.

2. Methods

2.1. Search Strategies

Relevant literature was systematically searched from online public databases (PubMed Central, Science Direct, and Scopus) using the following key-words: “Schistosomiasis” OR “S. mansoni” OR “S. haematobium” OR “parasitological study” OR “schistosome intermediate host” OR “freshwater snails” OR “malacological survey” OR “Biomphalaria snails” OR “Bulinus snails” AND “Africa”. The systematic review and selection of relevant literature were conducted according to PRISMA (Preferred Reporting Items for Systematic Reviews and Meta-analysis) guidelines [13] (Table S1).

2.2. Inclusion and Exclusion Criteria

Literature published in English language from 1979 to June 2020 were extracted from online public databases. Original articles reporting the prevalence of human schistosome cercariae in freshwater snails in African countries were included in the analysis. The eligibility for the inclusion of a study in our analysis had to fulfill the following criteria: (a) it was published in English, (b) the study was carried out in Africa, (c) the number of examined and infected snails with either S. mansoni or S. haematobium were clearly stated, and (d) snail species were identified at least to a genus level. Studies that reported nonhuman schistosome and other trematodes species were excluded from the analysis. Besides, review articles and meta-analysis were excluded from the analysis.

2.3. Data Extraction Protocol

The data extraction protocol was prepared and evaluated by all authors. From each published article, we extracted the following information: author information, year of publication, study country, snail species, number of snails (collected, examined and infected), the prevalence of snail infection, the type of schistosomes reported, and methods of schistosome’s detection.

2.4. Quality of Individual Study and Assessment of Bias

The quality of studies included in the meta-analysis was assessed by using the Newcastle–Ottawa quality assessment scale (NOS) proposed by Wells et al. [14] (Text S1). The quality assessment tool consists of three parts. First, the selection of study groups graded on a scale containing five stars; mainly deals with methodological qualities of individual study. Second, comparability of groups graded on a scale containing two stars; deals with comparability of studies based on design and analysis. Third, outcomes graded on a scale containing three stars, mainly focused on the assessment of the outcome and statistical analysis. Two authors (TH and EN) independently assessed the quality of individual study, and disagreement was solved by a discussion with the third author (AM). The overall quality of the individual study was categorized as high quality (≥8 stars), moderate quality (6-7 stars), and low quality (≤5 stars) by the total number stars obtained as described elsewhere [15].

2.5. Publication Bias across Studies

The risks of publication bias across studies were assessed using funnel plot symmetry qualitatively. Egger’s and Begg’s test were used to determine the presence of publication bias across studies quantitatively.

2.6. Data Analysis

We used a forest plot to estimate the overall pooled effect size with their 95% confidence interval (CI). The heterogeneity among studies used for this meta-analysis was evaluated using the I² test [16]. An I²- value lower than 25%, between 25% and 50%, and above 50% was regarded as low, moderate, and high heterogeneity, respectively [17]. Because of the high heterogeneity observed among the studies included in the meta-analysis, we used a random-effect model at 95% CI. To sort out the cause of heterogeneity, we used a subgroup analysis, sensitivity test, and meta-regression analysis. The data analysis was conducted using Stata software (version 14, STATA Corp College Station, TX), “metan” command.

3. Results

3.1. Search Results and Eligible Studies

A total of 2,995 relevant studies were screened from online public databases. Out of these studies, 976 articles were removed due to duplications while 1884 articles were excluded based on title and abstract screening. The remaining 135 full-text articles were assessed for eligibility. Of these, a total of 84 articles were excluded from the analysis based on specific exclusion criteria, and the remaining 51 articles were selected for this meta-analysis (Figure 1).

Figure 1: PRISMA flow diagram of for the inclusion of studies on the prevalence of S. mansoni and S. haematobium in freshwater snails in Africa.

3.2. Characteristics of Subjects in the Eligible Studies

The eligible articles were obtained from 17 African countries: Angola [18], Benin [19], Burkina Faso [20], Burundi [21], Chad [22], Côte d’Ivoire [23, 24], Egypt [25–30], Ethiopia [31–36], Kenya [37–39], Mali [40, 41], Niger [42, 43], Nigeria [44–54], Senegal [55, 56], Sudan [57], Tanzania [58–63], Uganda [64–67], and Zimbabwe [68]. Unfortunately, there were no studies from other African countries that fulfilled the inclusion criteria. Characteristics of the eligible article to this meta-analysis are presented in Table 1.

Table 1: Characteristic of the 51 eligible studies and pooled prevalences of S. mansoni and S. haematobium among freshwater snails in Africa included in this meta-analysis.

Author
Year
Country
Snail species
Snails examined (n)
Infected snails
Total
Schistosoma species
Quality score

Cercaria shedding (n)
Prevalence (%)
Screened by PCR
Positive (n)
Prevalence (%)
Infected snails (n)
Prevalence (%)

Sturrock et al. [39]
1979
Kenya
B. pfeifferi
938
65
6.93
—
—
—
65
6.93
S. mansoni
7

King et al. [30]
1982
Egypt
Bullines spp.
4312
9
0.21
—
—
—
9
0.21
S. haematobium
8

Lwambo [60]
1988
Tanzania
B. nasutus
17646
156
0.88
—
—
—
156
0.88
S. haematobium
9

Gryseels [21]
1991
Burundi
B. pfeifferi
29199
249
0.85
—
—
—
249
0.85
S. mansoni
9

Bado et al. [40]
1997
Mali
B. truncatus
266
-
-
266
22
8.30
22
8.3
S. haematobium
8

B. globosus
90
7
7.80
—
—
—
7
7.80
S. haematobium

Kariuki et al. [37]
2004
Kenya
B. nasutus
11000
122
1.20
—
—
—
122
1.20
S. haematobium
8

Kazibwe et al. [66]
2006
Uganda
B. stanleyi
21715
949
4.40
—
—
—
949
4.40
S. mansoni
9

B. sudanica
8452
296
3.50
—
—
—
296
3.50
S. mansoni

Hussien et al. [29]
2007
Egypt
B. alexandrina
2070
10
0.48
—
—
—
10
0.48
S. mansoni
8

Labbo et al. [43]
2007
Niger
B. forskalii
9450
5
0.05
—
—
—
5
0.05
S. haematobium
8

B. truncatus
27125
509
1.90
—
—
—
509
1.90
S. haematobium

Hussien et al. [25]
2008
Egypt
B. truncatus
837
14
1.67
—
—
—
14
1.67
S. haematobium
7

Odongo-Aginya et al. [64]
2008
Uganda
B. choanomphala
9194
164
1.78
—
—
—
164
1.78
S. mansoni
9

B. pfeifferi
4173
75
1.79
—
—
—
75
1.79
S. mansoni

Ayanda [47]
2009
Nigeria
B. globosus
392
72
18.37
—
—
—
72
18.37
S. haematobium
7

B. pfeifferi
256
52
20.31
—
—
—
52
20.31
S. mansoni

Ibikounlé et al. [19]
2009
Benin
B. pfeifferi
357
2
0.56
—
—
—
2
0.56
S. mansoni
8

Zongo et al. [20]
2009
Burkina Faso
B. truncatus
27
2
7.40
—
—
—
2
7.40
S. haematobium
7

Akinwale et al. [53]
2011
Nigeria
B. truncatus
138
—
—
138
41
29.70
41
29.70
S. haematobium
7

Lotf et al. [26]
2011
Egypt
B. alexandrina
277
17
6.10
—
—
—
17
6.10
S. mansoni
7

Mengistu et al. [34]
2011
Ethiopia
Biomphalaria spp.
560
325
58.00
—
—
—
325
58.00
S. mansoni
7

Opisa et al. [38]
2011
Kenya
B. pfeifferi
425
7
1.60
—
—
—
7
1.60
S. mansoni
9

B. sudanica
407
7
1.70
—
—
—
7
1.70
S. mansoni

B. globosus
227
5
2.20
—
—
—
5
2.20
S. haematobium

Abe et al. [50]
2012
Nigeria
B. truncatus
56
25
44.64
—
—
—
25
44.64
S. haematobium
7

Iboh et al. [48]
2012
Nigeria
B. globosus
120
13
10.80
—
—
—
13
10.80
S. haematobium
8

Mekonnen et al. [35]
2012
Ethiopia
B. pfeifferi
80
2
2.50
—
—
—
2
2.50
S. mansoni
7

Kinanpara [23]
2013
Côte d’Ivoire
B. globosus
189
23
12.17
—
—
—
23
12.17
S. haematobium
7

B pfeifferi
1409
25
1.77
—
—
—
25
1.77
S. mansoni

Alebie et al. [31]
2014
Ethiopia
B. pfeifferi
301
32
10.60
—
—
—
32
10.60
S. mansoni
7

Angelo et al. [62]
2014
Tanzania
B. sudanica
1470
11
0.75
—
—
—
11
0.75
S. mansoni
8

Ivoke et al. [49]
2014
Nigeria
B. globosus
308
62
20.10
—
—
—
62
20.10
S. haematobium
8

Moser et al. [22]
2014
Chad
B. truncatus
4119
1
0.80
—
—
—
1
0.02
S. haematobium
8

B. pfeifferi
108
1
0.90
—
—
—
1
0.90
S, mansoni

Akinwale et al. [54]
2015
Nigeria
B. globosus
109
—
—
109
38
34.80
38
34.80
S. haematobium
9

B. forskalii
22
—
—
22
8
36.40
8
36.40
S. haematobium

B. camerunensis
7
—
—
7
4
57.00
4
57.00
S. haematobium

B. senegalensis
11
—
—
11
2
18.20
2
18.20
S. haematobium

Amsalu et al. [33]
2015
Ethiopia
B. pfeifferi
31
1
3.20
—
—
—
1
3.20
S. mansoni
7

Bado et al. [41]
2015
Mali
B. truncatus
324
11
3.40
—
—
—
11
3.40
S. haematobium
8

B. pfeifferi
189
2
1.10
—
—
—
2
1.10
S. mansoni

Gashaw et al. [32]
2015
Ethiopia
B. pfeifferi
14
2
14.30
—
—
—
2
14.30
S. mansoni
7

Rowel et al., [67]
2015
Uganda
Biomphalaria spp
19355
127
0.70
—
—
—
127
0.70
S. mansoni
9

Senghor [55]
2015
Senegal
B. senegalensis
7333
8
0.11
—
—
—
8
0.11
S. haematobium
9

B. umbilicatus
339
22
6.51
—
—
—
22
6.51
S. haematobium

Aboelhadid et al. [27]
2016
Egypt
B. alexandrina
822
22
22.80
—
—
—
22
2.68
S. mansoni
7

B. truncatus
423
9
2.10
—
—
—
9
2.10
S. haematobium

Farghaly et al. [28]
2016
Egypt
B. alexandrina
400
3
0.8
400
13
3.3
13
3.3
S. mansoni
9

Mohammed et al. [57]
2016
Sudam
B. truncatus
1403
2
0.10
—
—
—
2
0.10
S. haematobium
9

B. pfeifferi
5100
82
1.60
—
—
—
82
1.60
S. mansoni

Pennance [63]
2016
Tanzania
B. globosus
1111
26
2.30
—
—
—
26
2.30
S. haematobium
8

Alemayehu et al. [36]
2017
Ethiopia
B. pfeifferi
111
7
6.30
—
—
—
7
6.30
S. mansoni
8

Allan et al. [18]
2017
Angola
B. globosus
173
25
14.50
—
—
—
25
14.50
S. haematobium
8

Bakuza et al. [69]
2017
Tanzania
B. pfeifferi
235
29
12.30
219
103
47.00
103
43.8
S. mansoni
8

Gouvras et al. [61]
2017
Tanzania
B. sudanica
35,910
439
1.21
—
—
—
439
1.21
S. mansoni
7

B. choanomphala
6906
61
0.88
—
—
—
61
0.88
S. mansoni

Okeke and Ubachukwu [52]
2017
Nigeria
B. pfeifferi
460
20
4.30
—
—
—
20
4.30
S. mansoni
8

Stanton et al. [65]
2017
Uganda
Biomphalaria spp.
499
5
1.00
118
22
18.64
27
5.4
S. mansoni
8

Aliyu et al. [51]
2018
Nigeria
B. pfeifferi
592
156
26.00
—
—
—
156
26.00
S. mansoni
8

B. truncatus
5942
1421
23.90
—
—
—
1421
23.90
S. haematobium

B. globosus
8894
2166
24.30
—
—
—
2166
24.30
S. haematobium

Afiukwa et al. [46]
2019
Nigeria
B. globosus
177
34
19.20
—
—
—
34
19.20
S. haematobium
8

B. truncatus
106
18
17.00
—
—
—
18
17.00
S. haematobium

Okeke et al. [45]
2019
Nigeria
B. pfeifferi
212
-
-
212
16
7.45
16
7.45
S. mansoni
8

Peletu et al. [44]
2019
Nigeria
B. globosus
112
5
4.50
—
—
—
5
4.50
S. haematobium
9

Rabone et al. [42]
2019
Niger
B. forskalii
11989
24
0.20
—
—
—
24
0.20
S. haematobium
9

B. pfeifferi
2290
79
3.40
—
—
—
79
3.40
S. mansoni

Tian-Bi et al. [24]
2019
Côte d’Ivoire
B. truncatus
1772
2
0.10
—
—
—
2
0.10
S. haematobium
9

B. globosus
247
5
2.00
—
—
—
5
2.00
S. haematobium

Catalano et al. [56]
2020
Senegal
B. pfeifferi
407
9
2.20
—
—
—
9
2.20
S. mansoni
7

Fuss et al. [59]
2020
Tanzania
B. sudanica
788
—
—
788
279
35.40
279
35.4
S. mansoni
9

Mutsaka-Makuvaza et al. [68]
2020
Zimbabwe
B. globosus
1542
30
1.90
—
—
—
30
1.90
S. haematobium
9

3.3. Risk of Bias within Studies

The Newcastle–Ottawa quality assessment scale indicated that there was no bias within studies. The individual study included in this review was moderate to high-quality score as indicated in Table 1.

3.4. Prevalence of S. mansoni and S. haematobium Cercaria Among Freshwater Snails

A total of 273, 643 snails from Biomphalaria and Bulinus genera were examined for the presence of S. mansoni and S. haematobium cercaria in the 51 eligible studies, respectively (Table 2). Out of these snails, 8,682 of them were infected by either S. mansoni or S. haematobium. The prevalence of schistosome cercaria in the individual study ranged from 0.05% to 58.03% with substantial heterogeneity across studies within and across countries. The pooled prevalence of schistosome cercaria among freshwater snails was 5.5% (95% CI: 4.9–6.1%, I² = 99.4%, and ) (Figure 2).

Table 2: The pooled prevalences of S. mansoni and S. haematobium infection among Biomphalaria and Bulinus snails of Africa.

Snail genus
Snail species
Studies (n)
Examined snails (n)
Infected snails

n
pp (95%CI)

Biomphalaria
B. pfeifferi
19
46480
987
5.10 (4.05–6.15)

B. sudanica
5
47027
1032
6.73 (4.46–9.01)

B. alexandrina
4
3569
62
2.81 (0.75–4.87)

B. choanomphala
2
16,100
225
1.58 (0.44–2.21)

B. stanleyi
1
21,715
949
4.37 (4.09–4.64)

Unclassified Biomphalaria snails
3
20414
479
21.28 (-1.78–44.34)

Bulinus
B. globosus
14
13691
2511
12.25 (6.23–18.27)

B. truncatus
13
42538
2077
5.78 (4.36–7.20)

B. nasutus
2
28648
278
0.98 (0.76–1.20)

B. senegalensis
2
7344
10
4.73 (-10.72–20.18)

B. umbilicatus
1
339
22
6.49 (3.71–9.27)

B. forskalii
3
21461
37
0.13 (0.08–0.34)

B. camerunensis
1
7
4
57.14 (21.30–92.99)

Unclassified Bulinus snails
1
4312
9
2.1 (0.10–3.90)

Total
51
273 643
8682
5.51 (4.95–6.07)

Figure 2: Forest plot diagram showing the prevalence of human infecting schistosomes (S. mansoni and S. haematobium) examined in snails in Africa. Each square represent effect size (ES) of individual studies, and the horizontal line represents the 95% CI. The diamond indicates the pooled effect and the vertical dash lines indicate the overall estimate.

3.5. Subgroup Analysis

The highest pooled prevalence of schistosome cercaria was observed among freshwater snails from Nigeria (19.0%; 95% CI: 12.7–25.3%), followed by Ethiopia (15.9%; 95% CI: −5.9–37.5%), Mali (5.2%; 95% CI: -0.3–10.7%), and Tanzania (4.9%; 95% CI: 3.8–6.0%) (Figure 3). We categorized the years of studies into four groups: before 2000, 2001 to 2010, 2011 to 2015, and 2016 to June 2020 to assess the trends on the prevalence of schistosome cercaria in freshwater snails. The pooled prevalence of schistosome cercaria among freshwater snails in years before 2000, 2001–2010, 2011–2015, and 2016–2020 was 1.3% (95% CI: 0.8–1.8%), 2.8% (95% CI: 1.8–3.8%), 6.1% (95% CI: 5.2–7%), and 8.3% (95% CI: 6.6–9.9%), respectively, in Africa (Figure 4).

Figure 3: Geographical distribution and pooled prevalence of S. mansoni and S. haematobium among Biomphalaria and Bulinus snails, respectively, in African countries.

Figure 4: The pooled prevalence of schistosome cercaria among freshwater snails in Africa based on year of publication.

This meta-analysis targets the two most common and widely distributed Schistosoma species (S. mansoni and S. haematobium) in the continent. Biomphalaria and Bulinus snails were the intermediate hosts for S. mansoni and S. haematobium, respectively. The pooled prevalence of S. mansoni cercaria in Biomphalaria snails was 5.6% (95% CI: 4.9–6.3%) while the pooled prevalence of S. haematobium cercaria in Bulinus snails was 5.2% (95% CI: 4.7–5.7%) (Figure 5).

Figure 5: Forest plot diagram showing the estimated effect size of S. mansoni in Biomphalaria snails and S. haematobium Bulinus snail in Africa.

The pooled prevalence of S. mansoni and S. haematobium among freshwater snails was varied from country to country. The highest pooled prevalence of S. mansoni among Biomphalaria snails was observed from Tanzania (16.6%) followed by Ethiopia (15.9%) and Nigeria (14.5%) (Figure S1). On the contrary, the highest pooled prevalence of S. haematobium among Bulinus snail was observed from Nigeria (19.6%) followed by Angola (14.5%) and Côte d’Ivoire (9.6%) (Figure S2).

Twelve snail species from Biomphalaria and Bulinus snails were reported in the eligible articles used for this meta-analysis (Table 2). Among these species, Biomphalaria pfeifferi was the most common snail species and reported from 19 studies (37.3%) from the total 51 studies included in this study. The pooled prevalence of S. mansoni cercaria was 5.1% (95% CI: 4.1–6.2%) among B. pfeifferi snails. Bulinus snail, particularly B. globosus and B. truncatus, were the second and third most reported snails species (reported in 14 and 13 studies, respectively) that serve as an intermediate host for S. haematobium. The pooled prevalence of S. haematobium cercaria was 12.3% (95% CI: 6.2–18.3%) and 5.8% (95% CI: 4.4–7.2%) in B. globosus and B. truncatus snails, respectively (Table 2).

The studies included in this meta-analysis used shedding of cercariae and PCR-based detection of schistosomes from snail tissue. The pooled prevalence of schistosomes obtained by shedding of cercariae was 4.5% (95% CI: 3.9–5.1%) in contrast to 26.7% (95% CI: 10.5–43.0%) obtained by PCR techniques (Figure 6).

Figure 6: Forest plot diagram showing the pooled prevalences of S. mansoni and S. haematobium among freshwater snails examined by cercarial shedding and PCR.

3.6. Publication Bias across Studies

The funnel plot symmetry demonstrates the presence of publication bias among studies included in this meta-analysis (Figure 7). Similarly, Egger’s test results () and Begg’s test () confirm the presence of publication bias among studies.

Figure 7: Funnel plot with 95% confidence limit showing publication bias across studies on the prevalence of S. mansoni and S. haematobium among freshwater snails of Africa.

3.7. Metaregression Analysis and Sensitivity Test

There were clear heterogeneities across studies included in this meta-analysis. We performed a meta-regression analysis to identify the sources of heterogeneity across studies. The metaregression analysis showed that methods of schistosome detection from snails (regression coefficient: 2.55, 95% CI, 1.17–5.54, ) might be the source of heterogeneity. The country of study (regression coefficient: 0.99, 95% CI, 0.89–1.11, ), years of publication (regression coefficient: 1.41, 95% CI, 0.91–2.18, ), snail genus (regression coefficient: 1.19, 95% CI, 0.56–2.55, ), and snail species (regression coefficient: 0.92, 95% CI, 0.8 ) did not contribute for the heterogeneity. Besides, a sensitivity analysis was performed by recalculating the pooled prevalence by sequentially removing one-by-one to assess the effect of individual studies to overall effect. The pooled prevalence remained stable, and the result was not driven by individual studies included in the meta-analysis.

4. Discussion

Schistosomiasis is the second leading cause of infectious diseases next to malaria in Africa. Despite intensive efforts to tackle schistosomiasis, the prevalence is still unacceptably high in many African countries. The control and prevention strategies mainly rely on treatment of infected cases and mass drug administration of school-aged children. In many African countries, snail control strategies are not routinely implemented and sometimes considered as old-fashion approaches [70] despite their vital contributions to the elimination of schistosomes witnessed from Japan, Iran, and Tunisia [71–73]. In addition, enormous progresses have been observed in the elimination program from Morocco, Oman, Lebanon, and Caribbean Islands [73, 74]. The intensity and prevalence of schistosomes’ infection among freshwater snails are scarce from many African countries. Summarized information about the prevalence of schistosomes among snail intermediate hosts is important for policymakers to give better attention to snail control strategies in Africa.

The overall pooled prevalence of schistosome cercaria was nearly 6% among freshwater snails in Africa. This finding is slightly lower than 9% reported from freshwater snails in Brazil [75]. In contrast, a lower prevalence of infected snails was observed from Indonesia [76] and Brazil [77]. These differences might be associated with prevalence and intensity of schistosome infection in the community, the level of environmental sanitation, suitability of the climate for the snails, level of existing snail control strategies, level of human exposure to open surface water, methods of schistosome detection, and seasons of snail collection and examination.

The highest pooled prevalence of schistosome cercaria among freshwater snails was observed in Nigeria followed by Ethiopia. In contrast, low prevalences of schistosomes were observed from Benin, Burundi, and Chad. The high prevalence of schistosomes among snail species in Nigeria and Ethiopia might be associated with the high prevalence of schistosomes in the community. The prevalence of schistosomiasis could reach as high as 90% in Ethiopia [78] and 94% in Nigeria [79, 80]. In addition, the difference in the level of environmental sanitation and the suitability of the area for the intermediate host, as well as the types of snail species in the area, may contribute for the difference in infection of snails across countries. Moreover, larger numbers of studies were reported from these two countries. Out of 51 studies, 17 (23.9%) studies included in this review were from the two countries.

Several species of freshwater snails that potentially serve as intermediate hosts for S. mansoni and S. haematobium have been recently reviewed [81]. Biomphalaria and Bulinus snails are the common and widely distributed intermediate hosts for schistosomes in Africa. The twelve snail species observed in this review belonged to either Biomphalaria or Bulinus genus.

Biomphalaria snails are well-known intermediate hosts of S. mansoni in Africa. This review showed that 5.6% of Biomphalaria snails were infected by S. mansoni in Africa. The highest pooled prevalence of S. mansoni was observed from Tanzania followed by Ethiopia and Nigeria, while low pooled prevalence was reported from Benin, Burundi, and Chad. These reported differences might be associated with the level of environmental sanitation, the abundance of Biomphalaria snails, and seasons of snail collection and examination. The highest prevalence of S. mansoni among Biomphalaria snails was reported during the dry season or just before the beginning of the rain seasons [47, 82].

Five species of Biomphalaria snails (B. pfeifferi, B. sudanica, B. choanomphala, B. alexandrina, and B. stanleyi) were included in the eligible articles for this review. As reviewed by Abe et al. [81], B. pfeifferi, B. sudanica, B. choanomphala, and B. alexandrina were the common intermediate hosts of S. mansoni in Africa. The pooled prevalence of S. mansoni varied from 1.3% to 6.7% among these snail species.

Biomphalaria pfeifferi were the most common snails infected by schistosome parasite. About 40% of the eligible studies included in this meta-analysis reported B. pfeifferi. The role of B. pfeifferi as an intermediate host of S. mansoni varied from country to country. Biomphalaria pfeifferi is the sole intermediate host for S. mansoni in Côte d’Ivoire [83] and Senegal [84] and the dominant intermediate host in many other African countries [85–88].

Biomphalaria sudanica was the second common Biomphalaria snails that serve as an intermediate host for S. mansoni as observed in this study. Biomphalaria sudanica is an intermediate host for S. mansoni in Kenya [47] and Tanzania [19, 89]. Biomphalaria sudanica is also reported from Ethiopia but limited to around Lake Ziway [90] and Tikur Wuha [87].

Biomphalaria alexandrina was the third common intermediate host for S. mansoni observed in this study. However, its contribution as an intermediate host for S. mansoni is restricted in geographical distribution, mainly reported from Egypt [91–93]. Biomphalaria choanomphala was another intermediate host for Schistosoma mansoni reported from Uganda [64] and Tanzania [61]. This snail species is widely distributed around Lake Victoria, which is divided among three countries (Kenya, Tanzania, and Uganda). Biomphalaria choanomphala is also reported from Kenya [94], but the infection intensity was not determined.

Bulinus snail is the common intermediate host for S. haematobium in Africa. This study revealed that about 5.2% of Bulinus snails were infected with S. haematobium in Africa. The highest pooled prevalence of S. haematobium infection among Bulinus snail was observed from Nigeria followed by Angola and Côte d’Ivoire. In contrast, there was a low prevalence of S. haematobium infection among Bulinus snails from Chad, Niger, Senegal, and Sudan. These variations might be associated with the difference in the level of endemicity of S. haematobium in the countries. A recent review indicated that about one-third of the populations of Nigeria were infected by S. haematobium [95, 96]. The higher infection intensity in the population might lead to a high level of environmental contamination that resulted in higher snail infection in Nigeria.

The eligible studies included in this review report seven species of Bulinus snails (B. truncates B. globosus, B. forskalii, B. senegalensis, B. nasutus, B. camerunensis, and B. umbilicatus) from African countries. According to Abe et al. [81], B. truncates, B. africanus, B. forskalii, B. senegalensis, and B. camerunensis were the predominant Bulinus snails that serve as an intermediate host for S. haematobium.

Among the Bulinus snails, B. globosus was reported from 14 studies in 7 African countries included in this review. The present study revealed that 12.3% of B. globosus was infected by S. haematobium. Similarly, high pooled prevalence (18%) of S. haematobium among B. globosus was recently reported in a meta-analysis from Nigeria [96]. Bulinus truncatus are the other important Bulinus snails that serve as an intermediate host for S. haematobium in Africa. The pooled prevalence of S. haematobium was 5.9% among Bulinus truncatus snails in Africa. In contrast to our result, 19% prevalence of S. haematobium was reported from B. truncates snails in Nigeria [31]. Similarly, B. truncatus is the predominant intermediate host for S. haematobium in Niger [42] and Côte d’Ivoire [23, 24].

Detection of schistosome infection is determined by shedding of cercariae and/or PCR based approaches from snail tissue. There was a significant difference in the pooled prevalence of schistosome results between shedding of cercaria (4.5%) and PCR (26.7%) among snail species in Africa. Similar differences (1.56% vs. 39.8%) are seen in the prevalence of schistosome infection between cercarial shedding and PCR methods among snails as reported from Kenya [97]. This difference is associated with the sensitivity of PCR to detect schistosome infection from snail tissue. Cercarial shedding is suffered by several limitations such as low parasite burden; snails may not shed cercariae during the prepatent period; time-consuming, and labour-intensive [98]. PCR-based detection of schistosome infection from snails is generally rapid, efficient, sensitive, and cost-effective for large-scale detection [99, 100].

Despite the ongoing schistosomiasis control strategies in many African countries, the pooled prevalence of schistosomes among freshwater snails had increased over time from 1.3% (before 2000) to 8.3% between 2016 and 2020. This might be attributed to the large number of epidemiological studies conducted and reported recently. Besides, molecular based detection of schistosome infection from snail tissue received attention in the recent years. These situations may contribute to the increased prevalence of schistosomes among freshwater snails recently.

4.1. Limitation of the Study

Although this systematic review generated valuable data on the prevalence of S. mansoni and S. haematobium among freshwater snails in Africa, it also has limitations. First, information on the prevalence of schistosome cercaria among snail species was not obtained from all African countries. Prevalence data were available only from 17 African countries. The pooled prevalences of schistosomes in this review may not fully represent the prevalence of S. mansoni and S. haematobium among freshwater snails of Africa. Second, the numbers of published studies were not evenly distributed even in the 17 countries (varied from 1 study to 11 studies in a country). Third, the studies included in this review were published in English, and we did not include studies published in other languages such as French due to language barriers and translation-related challenges. Fourth, most of the studies included in this review used cercarial shedding rather than PCR for the detection of schistosome infection. Cercarial shedding is less sensitive for the detection of schistosomes due to its inherent limitation that may result in low prevalence of schistosomes among infected snails in Africa. The pooled prevalence of schistosome cercaria among freshwater snails of Africa observed in this review might be below the actual infection intensity. Fifth, this review showed that there was high heterogeneity across studies included in this review. These might be associated with study design, seasons of snail collection, method of detection, and variation of endemicity of schistosomes across countries.

5. Conclusions

This review showed that nearly 6% of freshwater snails in Africa were infected by either S. haematobium or S. mansoni. The pooled prevalences of schistosome cercaria among freshwater snails have increased in the recent years in many African countries. The higher and increased trends in the prevalence of schistosomes among freshwater snails highlight the need for appropriate snail control strategies in the region. Policymakers should give better attention about integration of snail control strategies to the ongoing treatment-based prevention of schistosomiasis in Africa.

Abbreviations

CI: | Confidence interval
I²: | Inverse variance index
NOS: | Newcastle–Ottawa quality assessment scale
PRISMA: | Preferred Reporting Items for Systematic Reviews and Meta-analysis
PCR: | Polymerase chain reaction
NTD: | Neglected tropical disease.

Data Availability

All the datasets are included in the manuscript.

Conflicts of Interest

The authors declare that there are no conflicts of interest.

Authors’ Contributions

TH was involved in the design, conducted the review, data analysis, and interpretation of the findings, and drafted the manuscript. EN and AM were involved in drafting the manuscript, reviewing, and editing the manuscript.

Supplementary Materials

S1 Table: PRISMA checklist. S1 Text : NEWCASTLE–OTTAWA QUALITY ASSESSMENT SCALE. S1 Fig : forest plot showing the pooled effect estimate of S. mansoni among Biomphalaria snails in Africa. S2 Fig : forest plot showing the pooled prevalence estimate of S. haematobium among Bulinus snails in Africa. (Supplementary Materials)

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