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Prevalence of Schistosomes and Soil-Transmitted Helminths and Morbidity Associated with Schistosomiasis among Adult Population in Lake Victoria Basin, Tanzania

Prevalence of Schistosomes and Soil-Transmitted Helminths and Morbidity Associated with Schistosomiasis among Adult Population in Lake Victoria Basin, Tanzania

Article information

Korean J Parasito. 2015;53(5):525-533
Publication date (electronic) : 2015 October 29
doi : https://doi.org/10.3347/kjp.2015.53.5.525
1National Institute of Medical Research, P.O. Box 1462, Mwanza, Tanzania
2Department of Parasitology and Tropical Medicine, Seoul National University College of Medicine, Seoul 03080, Korea
3Department of Parasitology and Medical Research Institute, Chungbuk National University School of Medicine, Cheongju 28644, Korea
4Department of Parasitology, College of Medicine, Korea University, Seoul 02841, Korea
5Department of Environmental Medical Biology and Institute of Tropical Medicine, Yonsei University College of Medicine, Seoul 03722, Korea
6Department of Microbiology and Immunology, Eulji University College of Medicine, Daejeon 35233, Korea
7Good Neighbors International, Tanzania Western Chapter, P.O. Box 367, Mwanza, Tanzania
* Corresponding author (cjy@snu.ac.kr)
Received 2015 July 23; Revised 2015 September 30; Accepted 2015 October 4.

Abstract

The objective of this study was to carry out a community survey on schistosomiais and soil-transmitted helminth (STH) infections in order to suggest feasible and effective intervention strategies in Lake Victoria basin, Tanzania. A total of 37 communities selected from 23 districts of the 4 regions in the Lake Victoria basin of Tanzania were involved in the study. From each of the selected locality, 50 adult community members, 25 males and 25 females, were recruited for the study. Each study participant was requested to submit stool and urine specimens. From each stool specimen, duplicate Kato-Katz thick smears were prepared and microscopically examined for Schistosoma mansoni and STH eggs. Urine specimens were processed by the filtration technique and microscopically examined for Schistosoma haematobium eggs. Ultrasound examination for morbidity due to schistosomiasis was performed. Mass treatment was done using praziquantel and albendazole for schistosome and STHs infections, respectively. Out of 1,606 adults who provided stool specimens, 199 (12.4%) were positive for S. mansoni, 349 (21.7%) for hookworms, 133 (8.3%) for Ascaris lumbricoides, and 33 (2.0%) for Trichuris trichiura. Out of 1,400 participants who provided urine specimens, 25 (1.8%) were positive for S. haematobium eggs. Because of the co-endemicity of these afflictions and their impact on vulnerable population groups, the helminthiasis could be simultaneously treated with 2 drugs, praziquantel for schistosomiasis and albendazole for STHs.

INTRODUCTION

Human schistosomiasis is a disease caused by any of 5 species of trematodes, the blood flukes, in the genus Schistosoma, and infections are acquired by contact with freshwater containing parasite larvae. World Health Organization (WHO) estimates that over 237 million people required treatment for schistosomiasis in 2010 [1] with estimates of up to an additional 779 million at risk globally [2]. About 85% of the people at risk of schistosomiasis are from Africa [3] with more than 90% of the cases occurring in sub-Saharan Africa [4,5]. King [6] estimated that schistosome infections accounted for 24-56 million disability-adjusted life years (DALYs) lost in 2010.

Two major schistosome species are prevalent in sub-Saharan region, Schistosoma mansoni and Schistosoma haematobium causing intestinal and urogenital schistosomiasis, respectively [7,8]. Both types of schistosomiasis are hyper-endemic in the Great Lake regions of East Africa, owing to the favorable habitat for snails of Biomphalaria and Bulinus genera, which are the intermediate host for S. mansoni and S. haematobium, respectively [9]. Surveys have revealed the presence of the disease in other parts of the country, including Lake Victoria [9,10]. Lakeshore communities are typically dependent on water from these lakes, rivers, and ponds for various daily activities, including cooking, bathing, and washing clothes. Fishing is usually a major occupation of men of these communities, further bringing them into contact with water [11]. Historical studies have revealed that both schistosomiasis mansoni and schistosomiasis haematobium have been endemic for a long time in Tanzania [12,13]. Through a full consideration of the amount of end-organ pathologies to the liver (in the case of S. mansoni and S. japonicum infections) and bladder and kidneys (in the case of S. haematobium infection) [4], together with chronic morbidities associated with impaired child growth and development, chronic inflammation, anemia, and other nutritional deficiencies, some new disease burden assessments estimate that schistosmiasis accounts for up to 70 million DALYs lost annually [5].

WHO estimates that more than 1 billion people are chronically infected with soil-transmitted helminths (STHs) [14]. STHs persist exclusively in the poorest populations often living in remote, rural areas, urban slums, or in conflict zones [15]. Ascaris lumbricoides, hookworms (Ancylostoma duodenale and Necator americanus), and Trichuris trichiura are the most common STH species with global prevalence of about 1,000, 900-1,300, and 500 million cases, respectively [16-18].

Of the STH species, hookworms are the most widely distributed species occurring throughout much of East Africa [19]. Both schistosomiasis and STHs have long been known to be co-endemic in the Lake Victoria basin in Tanzania [4,20,21]. A comaparable situation has been reported in the Kenya [5,22] and Uganda sides of the basin. A. lumbricoides and T. trichuria have the highest prevalences in areas close to Lake Victoria of Tanzania, western Kenya, and southeastern Uganda [19,23].

The morbidity caused by STHs is most commonly associated with infections of moderate-to-heavy intensities [24,25]. Several studies have revealed the impact of STH infections as significant predictors of protein-energy malnutrition, iron-deficiency anemia (IDA), vitamin A deficiency (VAD), and poor academic performance among schoolchildren in different countries [26-29]. Moreover, these consequences may continue into adulthood with effects on the economic productivity which trap the communities at risk of infections in a cycle of poverty, underdevelopment, and disease [30]. Hence, benefits of successful STH control programmes extend well beyond eliminating STH as they improve the nutritional and health status of children as well as contribute to higher educational attainment, labor force participation, productivity, and income among the most vulnerable populations [31-33].

Schistosomes and STH-immunosuppressive features have possible impact on promoting susceptibility to HIV/AIDS, tuberculosis, and malaria [34,35], and there is evidence that female genital schistosomiasis caused by S. haematobium may significantly increase the likelihood of contracting HIV/AIDS [22]. Moreover, there are adverse effects on pregnancy outcome and agricultural worker productivity [2,6,36-39]; helminths are strongly associated with poverty in sub-Saharan Africa. Therefore, new and ongoing efforts to control and eliminate helminths and neglected tropical diseases (NTDs) generally represent key elements for achieving Africa's Millennium Development Goals (MDGs) [2,36]. As such, the successful STH control programmes have enormous benefits of improved nutritional and health status of children for higher educational attainment, labor force participation, productivity, and income among the most vulnerable populations [33,41]. Mass drug administration (MDA) has been a major approach to control human helminthiases in developing countries [42]. In order to control schistosomiasis and STHs, WHO recommends MDA if the prevalence exceeds 10% and has the target of deworming at least 75% of school-aged children and other high-risk groups by administration with praziquantel for schistosomes and albendazole or mebendazole for STHs [22].

Conversely, control of helminth infections has been suggested as the means to facilitate control of the big 3 species [43,44], especially by reducing the frequency of malaria fevers, the frequency of severe and cerebral malaria, and the prevalence of anemia [45-47]. Furthermore, new evidence points to substantial geographic overlap between NTDs and the big 3 helminthic diseases, with emerging data suggesting that control of NTDs could actually become a powerful tool for combating HIV/AIDS, tuberculosis, and malaria [48]. The main objective of this study was to carry out a survey on schistosomiasis and STHs in order to suggest feasible and effective intervention strategies in the Lake Victoria basin, Tanzania.

MATERIALS AND METHODS

Study area and population

The study area is the basin of Lake Victoria located on the northwest of Tanzania (Fig. 1). The area stretches from the west through south to the eastern side of the lake. It is comprised with Kagera, Mwanza, and Mara on the lake shore and Shinyanga about 60 km away from the lake. The study area is bordered by Uganda on the north, and Rwanda and Burundi on the west. The main ethnic groups include Wahaya, Wasukuma, Wazinza, Wakerewe, Wajita, Wakurya, and Waluo. The major occupations of these people are peasant farming, pastoralism, and fishing. Much of the activities have a bearing to schistosomiasis and STH infections as they are performed without protective gear. The level of sanitation and hygiene in the area is as low as in any poor resource settings.

Fig. 1.

Map of the study areas. Localities in Kagera region (1. Bunena, 2. Kiziramuyaga, 3. Kyenshama, 4. Nyairigamba, 5. Buzirayombo, 6. Bwanga, 7. Bwina, 8. Runazi, and 9. Kahengere), Mwanza region (10. Tumaini, 11. Mazoezi, 12. Lumeji, 13. Nyamikoma, 14. Mwaging’hi, 15. Kigongo, 16. Bugogo, 17. Chibingo, 18. Kasamwa, 19. Nyakalilo, 20. Bungonya, and 21. Busisi), Mara region (22. Gamasara, 23. Ochuna, 24. Marasibora, 25. Minigo, 26. Mwisenge, 27. Guta “A”, 28. Nyamitwebili, and 29. Bulamba), and Shinyanga region (30. Mseki, 31. Bukomela, 32. Masumbwe, 33. Luhumbo, 34. Songwa, 35. Shishiyu, 36. Ngugunu, and 37. Sapiwi).

Specimen collection and examinations

Collection of stool and urine specimens was done at the selected schools where inhabitants visited. Each village person was given 1 stool container and 1 urine container on the first day and asked to bring the urine and stool specimens. The stool samples collected were processed to make duplicate Kato-Katz thick smears covered with cellophane soaked in glycerine and malachite green [49]. The smears were examined for hookworms and other helminth eggs or larvae within 1 hr after preparation. Examination for S. mansoni eggs were done a few minutes later. The egg counts on each of the 2 slides were added together and divided by 2 to get the mean number of egg counts.

Urine samples were collected after 10.00 a.m. to diagnose S. haematobium based on detection of eggs in urine using the filtration technique with nuclepore membranes according to WHO [21]. Urine samples were mixed thoroughly and 10 ml were drawn using a syringe and passed through the membrane where eggs were logged. Examination was done on site where detected eggs were counted and expressed as the number of eggs per 10 ml of urine.

Data management and analysis

Data entry was done using Dbase IV (Borland International, Scotts Valley, California, USA) and a double entry system was used for quality control. Data was transferred to STATA version 8 software (Statacorp 2000, College Station, Texas, USA) for analysis. Analysis was done by generation of some frequency tables, cross tabulations, and calculation of prevalence.

Ethical considerations

The ethical and scientific clearance was obtained from the Medical Research Coordinating Committee of the National Institute for Medical Research before the implementation of the study. The study team visited villages where community leaders were met and the objectives, procedure, potential harm, and benefits of the study were explained to them. The leaders in turn convened meetings of the community members and the same was explained to them before the consent to participate in the study was sought. Any participant would be free to withdraw from the study at any time of the study period when he or she felt to do so. The decision to refuse or withdraw from the study would have no negative effect on benefits provided during and after the study.

All subjects who would be found infected with schistosomiasis or intestinal helminths would be treated following standard treatment guidelines. Participants were informed that information will be confidentially kept only using code numbers instead of names of participants.

RESULTS

A total of 1,606 from 36 selected communities, mostly from the shoreline of the Lake Victoria basin in Tanzania, were recruited for the study (Table 1). Out of 1,606 adults who provided stool specimens, 199 (12.4%) were positive for S. mansoni, 349 (21.7) for hookworms, 133 (8.3%) for A. lumbricoides, and 33 (2.0%) for T. trichiura. A total of 1,400 adults provided urine for S. haematobium diagnosis out of whom 25 (1.8%) from Mwanza and Mara were positive for eggs (Table 1). The highest prevalence (18.9%) of intestinal schistosomiasis were recorded in Mwanza region followed by Kagera with 17.8%. No intestinal schistosomiasis was found among study participants from Shinyanga. It was only in Kagera region that all the 3 common STHs at various prevalence rates were found.

Mean prevalence of schistosomes and soil-transmitted helminths among adult population in Lake Victoria basin, Tanzania

Interestingly, no schistosomiasis haematobium patient was recorded in Shinyanga region despite its being located in the hinterland. Shinyanga is naturally the driest of the 4 regions, and the study was done in mid-July during draught when S. haematobium transmission is low.

The few adult members with urogenital infections observed in Mwanza and Mara were from wet areas with paddy fields. Such areas are good habitats for snail hosts of the genus Bulinus. By that time Bulamba locality was dry besides being close to the lake.

The study team visited a total of 9 localities in 5 out of 8 districts in Kagera region. In this region, 488 adults provided stool specimens. In total, 87 (17.8%) were positive for intestinal schistosomiasis, 182 (37.3%) for hookworms, 113 (23.2%) for ascariasis, and 33 (6.8%) for trichuriasis (Table 2). The highest prevalence (77.1%) of intestinal schistosomiasis was recorded at Bwina locality in Chato District followed by Bwanga (30.3%) and Kiziramuyaga (18.5%) in Chato and Muleba Districts, respectively. Hookworm infections were the highest at Runazi (69.6%), Bwina (68.8%), and Kiziramuyaga (66.2%) in Biharamulo, Chato, and Muleba Districts, respectively. The prevalence of ascariasis was the highest at Kyenshama (66.0%) in Muleba District, followed by an urban community of Bunena (42.9%), then Bwina (31.3%) and Bwanga (24.2%), both in Chato District. Trichuriasis was highly prevalent at Bunena (33.3%) in Bukoba Urban District (Table 2). We could not record any urogenital schistosomiasis case in this region.

Prevalence of schistosomes and soil-transmitted helminths among adult population in Kagera region

The study team visited a total of 12 communities from 7 of the 8 districts of Mwanza region. Out of 471 adult participants who provided stool specimens, 89 (18.9%) had intestinal schistosomiasis and 42 (8.9%) had hookworms. No one was found to be infected with Ascaris, Trichuris, or other intestinal helminths (Table 3). Out of 265 adults who had their urine specimen examined, only 3 (1.1%) from 2 communities of Geita had urogenital schistosomiasis. About a half (51.1%) of those who presented stools at Bungonya in Sengerema had intestinal schistosomiasis. Six of 14 individuals (42.9%) at Tumaini in Ilemala and 21 out of 50 examinees (42.0%) at Nyamikoma in Magu District were found infected with intestinal schistosomiasis. Mwaging’hi in Kwimba District recorded the highest prevalence of hookworms (50.0%) followed by Tumaini (35.7%) and Lumeji (21.6%) in Ilemela and Magu Districts, respectively (Table 3).

Prevalence of helminths in stool and urine samples among adult population in selected localities in Mwanza region

We recruited 344 adult members from Mara region who provided both stool and urine specimens. The region had relatively low prevalence (6.7%) of S. mansoni and even lower prevalence (0.9%) of hookworms. Only 22 (6.4%) were positive for S. haematobium (Table 4). The highest recorded prevalence of intestinal schistosomiasis in the region was from Nyamitwebili where out of 44 members who provided stool specimens, 8 (18.2%) were positive for the disease. Mwisenge locality was the second by having 7 (13.7%) positive cases for the disease. Other localities had less than 10% prevalence (Table 4). Of STHs, only hookworms were recorded at Minigo in Rorya District and Mwisenge in Musoma Urban Districts. With the exception of Bulamba in Bunda District, all communities in Mara region had cases infected with S. haematobium. The prevalence was the highest (18.2%) at Minigo community in Rorya District.

Prevalence of schistosomes and soil-transmitted helminths among adult population in Mara region

Shinyanga region had totally different findings from the other 3 regions. In this region, out of 303 members who provided both stool and urine specimens, only 33 (10.9%) were positive for hookworm eggs (Table 5). The highest prevalence for hookworms was found in Kahama District at Bukomela and Mseki localities with 40.4% and 33.3% prevalence, respectively (Table 5). No other STH infections were found. Neither could we find a person infected with intestinal or urogenital shistosomiases.

Prevalence of parasites among adult population in various localities in Shinyanga region

DISCUSSION

The study results showed that generally the prevalence of S. mansoni, S. haematobium, and STHs is widespread in the study area. This observation agrees to the findings of earlier studies in the area [36,50]. However, the prevalence of S. mansoni in Kagera region was very low with the exception of a few pockets in Chato District. This could be attributed to the fact that lake shores in Kagera region are open ones instead of bays such that when the wind blows makes the waves splash the shores making the place an unconduncive habitat for snail intermediate hosts for schistosomes. Moreover, some of the shores in Kagera region are formed by escarpments thus deep and less habitable by the snails. The situation is quite different from shores in Chato District in the southwest of Lake Victoria which are mainly shallow and in bays thus not susceptible to strong winds and can habor the snails. The relatively higher prevalence of ascariasis and trichuriasis in Kagera region than in other regions could be attributed to the difference in soil temperature, altitude, soil type, and rainfall [51-53]. Kagera region is wet almost throughout the year as compared to the rest of the regions in the area. The highest prevalence of S. mansoni in Kagera region that was recorded at Bwina community could be attributed to the location of the study site. Bwina ward is a thin peninsular with an average width of less than 2 km. As such, most of the area is surrounded by Lake Victoria water that is inhabited by the snail intermediate host Biomphararia species for S. mansoni. Bwanga and Kiziramuyaga localities are close to the lake area that has small bays that are conduncive areas for the snail hosts. This has an implication of the region having the best breeding ground of the STHs as well as more people consuming more vegetables that may be carrying the helminth eggs than those from other areas. The absence of urogenital schistosomiasis in Kagera could be due to an absence of ponds and streams during the time of the study, and the fact that no paddy cultivation is practiced in the area.

The high prevalence of intestinal and urogenital schistosomisiasis in the study area was a function of the distance from Lake Victoria; the former being more prevalent at localities close to the lake, whilist the latter is more so away from it. Similar observations had been reported elsewhere in East Africa [17,19,28,29,54]. The high prevalence of intestinal schistosomiasis at Nyamitwebili and Mwisenge localities could be associated with their being at the lake shore. Minigo had a lot of paddy fields that are good habitats for snail intermediate hosts for S. haematobium. The distribution of S. haematobium and S. mansoni along Lake Victoria is largely related to the distribution of the intermediate hosts [53]. Along the shore of the lake, members of the genus Biomphalaria are common [54,55] with populations living along the lake shores and islands being highly affected by S. mansoni, as the risk of infection increases [56].

In Mara region, the distribution of S. mansoni was similar to that of Mwanza with more S. mansoni close to the lake and S. haematobium on the hinterland. Moreover, in areas where S. haematobium was high, there was a significant prevalence of hookworms. The findings are in line with the ones from a previous study in Magu District in Mwanza region [35]. The spatial distribution of S. haematobium and hookworm is in accordance with the presence of ponds and streams as well as wetness and warmth of the soil in the reference area that are prerequisite for proliferation of the 2 helminths.

We could not easily establish why there were no infections due to A. lumbricoides and T. trichiura in Mwanza region or intestinal schistosomiasis in Shinyanga region. A major reason could be geographical as stated above or there were treatment programmes prior to this study.

The study results showed that schistosomiasis and 3 STHs infections (hookworms, Ascaris, and Trichuris) were co-endemic in Lake Victoria basin in Tanzania with a high probability of polyparasitism in the study participants. The prevalence of S. mansoni, S. haematobium, and STHs ranged from low to moderate in most parts of the study area. Intestinal schistosomiasis was prevalent along the Lake Victoria shores and decreased with distance from it. Conversely, the prevalence of urogenital schistosomiasis increased with distance from the Lake. The distributions of both schistosome and geohelminth infections have important implications for integrated intervention including periodic community deworming programmes, provision of safe water supply, and proper health education relevant to good personal hygiene and good sanitary practices. These activities will facilitate the reduction of both prevalence and intensity of infections of schistosomiasis and STHs in such endemic communities. Pre- and post-intervention studies to assess knowledge, attitude, and practices of the concerned population cannot be overemphasized.

Acknowledgements

The authors are very grateful to the people of Kagera, Mwanza, Mara, and Shinyanga for their tireless commitment to participate in the study for all 5 years running. Our heartfelt thanks go to the Government of the Republic of Korea through the Korea international Cooperation Agency (KOICA). Good Neighbors International (GNI) funded the study and provided expertise for conduction of the study from the beginning to its logical conclusion. Particular gratitude is extended to the staff of NIMR, Mwanza Research Center, and entire members of GNI Tanzania Western Chapter for their material, moral, and technical support during the study. We would like to thank all those who supported us in one way or another for their commitments and deligency during all the stages of the study.

Notes

The authors declared no conflict of interest whatsoever.

References

1. World Health Organization. Schistosomiasis: population requiring preventive chemotherapy and number of people treated in 2010. Weekly Epidemiol Rec 2012;87:37–44.
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;6:411–425.
3. Chitsulo L, Engels D, Montresor A, Savioli L. The global status of schistosomiasis and its control. Acta Trop 2000;77:41–51.
4. van der Werf MJ, de Vlas SJ, Brooker S, Looman CW, Nagelkerke NJ, Habbema JD, Engels D. Quantification of clinical morbidity associated with schistosome infection in sub-Saharan Africa. Acta Trop 2003;86:125–139.
5. King CH, Dangerfield-Cha M. The unacknowledged impact of chronic schistosomiasis. Chronic Illn 2008;4:65–79.
6. King CH. Parasites and poverty: the case of schistosomiasis. Acta Trop 2010;113:95–104.
7. World Health Organization. Schistosomiasis and soil-transmitted infections. 54th World Health Assembly, agenda item 13.3 resolution. WHO 54.19 2001.
8. World Health Organization: Reducing risks, promoting healthy life. The World Health Report 2002. In Burden of disease in DAILYs by cause, sex and mortality stratums in WHO regions, estimates for 2001 Geneva, Switzerland: World Health Organization; 2002.
9. Morgan JAT, Dejong RJ, Snyder SD, Mkoji GM, Loker ES. Schistosoma mansoni and Biomphalaria: past history and future trends. Parasitology 2001;123:S211–S228.
10. Aginya EIO, Doering E. Epidemiology, of bilharzias (schistosomiasis) in Uganda from 1902 until 2005. Afr Health Sci 2008;8:239–243.
11. Reynolds JE, Kitakule JA. Field document No. 2: socioeconomic aspects of Lake Victoria and Albert fisheries: the 1991 FISHIN’ community survey. FISHING Notes and Records Rome, Italy: FAO/UNDP; 1991.
12. Snow RW, Guerra CA, Noor AM, Myint HY, Hay SI. The global distribution of clinical episodes of Plasmodium falciparum malaria. Nature 2005;434:214–217.
13. Ministry of Health. In : Annual Health Statistics Abstract. Ministry of Health and Social Welfare, Dar es Salaam, United Republic of Tanzania; 2002.
14. Montresor A, Crompton DWT, Hall A, Bundy DAP. Guidelines for the evaluation of soil-transmitted helminthiasis and schistosomiasis at community level, WHO/CTD/SIP/98.1 Geneva, Switzerland: World Health Organization; 1998.
15. Hotez PJ, Fenwick A, Savioli L, Molyneux DH. Rescuing the bottom billion through control of neglected tropical diseases. Lancet 2009;373:1570–1575.
16. Hotez PJ, Ehrenberg JP. Escalating the global fight against neglected tropical diseases through interventions in the Asia Pacific region. Adv Parasitol 2010;72:31–53.
17. World Health Organization. Soil-transmitted helminthiases. Eliminating soil-transmitted helminthiases as a public health problem in children. Progress report 2001-2010 and strategic plan 2011-2020 Geneva, Switzerland: World Health Organization; 2012.
18. Brooker S, Clements AC, Bundy DA. Global epidemiology, ecology and control of soil-transmitted helminth infection. Adv Parasitol 2006;62:221–261.
19. Brooker S, Kabatereine NB, Smith JL, Mupfasoni D, Mwanje MT, Ndayishimiye O, Lwambo NJ, Mbotha D, Karanja P, Mwandawiro C, Muchiri E, Clements AC, Bundy DA, Snow RW. An updated atlas of human helminth infections: the example of East Africa. Int J Health Geogr 2009;8:42.
20. Taylor-Robinson DC, Jones AP, Garner P. Deworming drugs for treating soil-transmitted intestinal worms in children: effects on growth and school performance. Cochrane Database Syst Rev 2007;(4):CD000371.
21. World Health Organization. Prevention and control of schistosomiasis and soil-transmitted helminthiasis: report of a WHO expert committee Geneva, Switzerland: World Health Organization; 2002.
22. Kjetland EF, Ndhlovu PD, Gorno E, Mduluza T, Midzi N, Gwanzura L, Mason PR, Sandvik L, Friis H, Gundersen SG. Association between genital schistosomiasis and HIV in rural Zimbabwean women. AIDS 2006;20:593–600.
23. Handzel T, Karanja DM, Addiss DG, Hightower AW, Rosen DH, Colley DG, Andove J, Slutsker L, Secor WE. Geographic distribution of schistosomiasis and soil-transmitted helminths in Western Kenya: implications for anthelminthic mass treatment. Am J Trop Med Hyg 2003;69:318–323.
24. Ahmed A, Al-Mekhlafi HM, Choy SH, Ithoi I, Al-Adhroey AH, Abdulsalam AM, Surin J. The burden of moderate-to-heavy soiltransmitted helminth infections among rural Malaysian aborigines: an urgent need for an integrated control programme. Parasit Vectors 2011;4:242.
25. Nokes C, Grantham-McGregor SM, Sawyer A, Cooper ES, Robinson BA, Bundy DA. Moderate to heavy infections of Trichuris trichiura affect cognitive function in Jamaican school children. Parasitology 1992;104:539–547.
26. Al-Mekhlafi HMS, Azlin M, NorAini U, Shaik A, Sa’aih A, Fatmah A, Ismail MG, Ahmad Firdaus MS, Aisah MY, Rozlida AR, Moktar N. Malnutrition and soil-transmitted helminthiasis among Orang Asli children in Selangor, Malaysia. Asia Pac J Clin Nutr 2005;14:188–194.
27. World Health Organization. De-worming for health and development. Report of the third global meeting of the partners for parasite control Geneva, Switzerland: World Health Organization; 2005.
28. Dreyfuss ML, Stoltzfus RJ, Shrestha JB, Pradhan EK, LeClerq SC, Khatry SK, Shrestha SR, Katz J, Albonico M, West KP Jr. Hookworms, malaria and vitamin A deficiency contribute to anemia and iron deficiency among pregnant women in the plains of Nepal. Nutr 2000;130:2527–2536.
29. Guyatt H. Do intestinal nematodes affect productivity in adulthood? Parasitol Today 2000;16:153–158.
30. Bleakley H. Disease and development: evidence from hookworm eradication in the American South. Quart J Econom 2007;122:73–117.
31. Kamel M, Ghafar Y, Foda N, Khashab S. Impact of type and stage of schistosomiasis on quality of life and productivity of infected workers. J Egypt Soc Parasitol 2001;3:153–167.
32. Conteh L, Engels T, Molyneux DH. Socioeconomic aspects of neglected tropical diseases. Lancet 2010;375:239–247.
33. Molyneux DH, Malecela MN. Neglected tropical diseases and the millennium development goals: why the “other diseases” matter: reality versus rhetoric. Parasit Vectors 2011;4:234.
34. Richter J. The impact of chemotherapy on morbidity due to schistosomiasis. Acta Trop 2003;86:161–183.
35. Lwambo NJ, Siza JE, Brooker S, Bundy DA, Guyatt H. Patterns of concurrent hookworm infection and schistosomiasis in schoolchildren in Tanzania. Trans R Soc Trop Med Hyg 1999;93:497–502.
36. Muller R. Worms and Human Disease Wallingford, UK: CABI Publishing; 2002.
37. Brooker S, Bundy DAP. Soil-transmitted helminths (geohelminths) In Cook GC, Zumla AI, eds, Manson's Tropical Diseases London, UK: Elsevier; 2008. p. 848–853.
38. Hotez PJ, Bundy DAP, Beegle K, Brooker S, Drake L, de Silva N, Montresor A, Engels D, Jukes M, Chitsulo L, Chow J, Laxminarayan R, Michaud C, Bethony J, Oliveira R, Xiao SH, Fenwick A, Savioli L. Helminth Infections: soil-transmitted helminth infections and schistosomiasis. In : Jamison DT, Breman J, Measham AR, Alleyne G, Claeson M, Evans DB, Jha P, Mills A, Musgrove P, eds. Disease Control Priorities in Developing Countries New York, USA: Oxford University Press; 2006. p. 467–497.
39. Keiser J, Utzinger J. Efficacy of current drugs against soil-transmitted helminth infections: systematic review and meta-analysis. JAMA 2008;299:1937–1948.
40. Kamel M, Ghafar Y, Foda N, Khashab S. Impact of type and stage of schistosomiasis on quality of life and productivity of infected workers. J Egypt Soc Parasitol 2001;3:153–167.
41. Conteh L, Engels T, Molyneux DH. Socioeconomic aspects of neglected tropical diseases. Lancet 2010;375:239–247.
42. Hotez PJ, Molyneux DH, Fenwick A, Kumaresan J, Sachs SE, Sachs JD, Savioli L. Control of neglected tropical diseases. N Engl J Med 2007;357:1018–1027.
43. Fincham JE, Markus MB, Adams VJ. Could control of soil-transmitted helminthic infection influence the HIV/AIDS pandemic. Acta Trop 2003;86:315–333.
44. Druilhe P, Tall A, Sokhna C. Worms can worsen malaria: towards a new means to roll back malaria? Trends Parasitol 2005;21:359–362.
45. Spiegel A, Tall A, Raphenson G, Trape J-F, Druilhe P. Increased frequency of malaria attacks in subjects co-infected by intestinal worms and Plasmodium falciparum. Trans R Soc Trop Med Hyg 2003;97:198–199.
46. Le Hesran JK, Akiana J, Ndiaye el HM, Dia M, Senghor P, Konate L. Severe malaria attack is associated with high prevalence of Ascaris lumbricoides infection among children in rural Senegal. Trans R Soc Trop Med Hyg 2004;98:397–399.
47. Christian P, Khatry SK, West KP. Antenatal anthelminthic treatment, birthweight, and infant survival in rural Nepal. Lancet 2004;364:981–983.
48. Hotez PJ, Molyneux DH, Fenwick A, Ottesen E, Ehrlich Sachs S, Sachs JD. Incorporating a rapid-impact package for neglected tropical diseases with programs for HIV/AIDS, tuberculosis, and malaria. PLoS Med 2006;3e102.
49. Katz N, Chaves A, Pellegrino J. A simple device for quantitative stool thick-smear technique in schistosomiasis mansoni. Rev Inst Med Trop Sao Paulo 1972;14:397–400.
50. Mazigo HD, Waihenya R, Lwambo NJS, Mnyone LL, Mahande AM, Seni J, Zinga M, Kapesa A, Kweka EJ, Mshana SE, Heukelbach J, Mkoji GM. Co-infections with Plasmodium falciparum, Schistosoma mansoni and intestinal helminths among schoolchildren in endemic areas of northwestern Tanzania. Parasit Vectors 2010;3:44.
51. Hotez PJ, Brindley PJ, Bethony JM, King CH, Pearce EJ, Jaconson J. Helminth infections: the great neglected tropical diseases. J Clin Invest 2008;118:1311–1321.
52. Appleton CC, Gouws E. The distribution of common intestinal nematodes along an altitudinal transect in KwaZulu-Natal, South Africa. Ann Trop Med Parasitol 1996;90:181–188.
53. Kariuki HC, Clennon JA, Brady MS, Kitron U, Sturrock RF, Ouma JH, Ndzovu ST, Mungai P, Hoffman O, Hamburger J, Pellegrini C, Muchiri EM, King CH. Distribution patterns and cercarial shedding of Bulinus nasutus and other snails in the Msambweni area, Coast Province, Kenya. Am J Trop Med Hyg 2004;70:449–456.
54. Jordan P, Webbe G. Epidemiology. In Schistosomiasis, Epidemiology, Treatment and Control London, UK: Heinemann Medical Books; 1982. p. 227–229.
55. Magendantz M. The biology of Biomphalaria choanomphala and B. sudanica in relation to their role in the transmission of Schistosoma mansoni in Lake Victoria at Mwanza, Tanzania. Bull World Health Organ 1972;47:331–342.
56. Marti HP, Tanner HP, DegreÂmont AA, Freyvogel TA. Studies on the ecology of Bulinus globosus, the intermediate host of Schistosoma haematobium, the Ifakara area, Tanzania. Acta Trop 1985;42:171–187.

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Fig. 1.

Map of the study areas. Localities in Kagera region (1. Bunena, 2. Kiziramuyaga, 3. Kyenshama, 4. Nyairigamba, 5. Buzirayombo, 6. Bwanga, 7. Bwina, 8. Runazi, and 9. Kahengere), Mwanza region (10. Tumaini, 11. Mazoezi, 12. Lumeji, 13. Nyamikoma, 14. Mwaging’hi, 15. Kigongo, 16. Bugogo, 17. Chibingo, 18. Kasamwa, 19. Nyakalilo, 20. Bungonya, and 21. Busisi), Mara region (22. Gamasara, 23. Ochuna, 24. Marasibora, 25. Minigo, 26. Mwisenge, 27. Guta “A”, 28. Nyamitwebili, and 29. Bulamba), and Shinyanga region (30. Mseki, 31. Bukomela, 32. Masumbwe, 33. Luhumbo, 34. Songwa, 35. Shishiyu, 36. Ngugunu, and 37. Sapiwi).

Table 1.

Mean prevalence of schistosomes and soil-transmitted helminths among adult population in Lake Victoria basin, Tanzania

Region Helminth eggs in stool
S. haematobium eggs in urine
No. exam. S. mansoni
Hookworms
A. lumbricoides
T. trichiura
No. exam. No. posit. (%)
No. posit. (%) No. posit. (%) No. posit. (%) No. posit. (%)
Kagera 488 87 (17.8) 182 (37.3) 113 (23.2) 33 (6.7) 488 0 (0.0)
Mwanza 471 89 (18.9) 42 (8.9) 0 (0.0) 0 (0.0) 265 3 (1.1)
Mara 344 23 (6.7) 3 (0.9) 0 (0.0) 0 (0.0) 344 22 (6.4)
Shinyanga 303 0 (0.0) 122 (40.3) 0 (0.0) 0 (0.0) 303 0 (0.0)
Total 1,606 199 (12.4) 349 (21.7) 133 (8.3) 33 (2.0) 1,400 25 (1.8)

Table 2.

Prevalence of schistosomes and soil-transmitted helminths among adult population in Kagera region

District Locality Helminth eggs in stool
No. exam. S. mansoni
Hookworms
A. lumbricoides
T. trichiura
No. posit. (%) No. posit. (%) No. posit. (%) No. posit. (%)
Bukoba urban Bunena 42 4 (9.5) 2 (4.8) 18 (42.9) 14 (33.3)
Muleba Kiziramuyaga 65 12 (18.5) 43 (66.2) 0 (0.0) 5 (7.7)
Muleba Kyenshama 47 4 (8.5) 12 (25.5) 31 (66.0) 4 (8.5)
Muleba Nyairigamba 53 5 (9.4) 3 (5.7) 9 (17.0) 2 (3.8)
Chato Buzirayombo 90 12 (13.3) 33 (36.7) 6 (6.7) 0 (0.0)
Chato Bwanga 33 10 (30.3) 3 (9.1) 8 (24.2) 1 (3.0)
Chato Bwina 48 37 (77.1) 33 (68.8) 15 (31.3) 3 (6.3)
Biharamulo Runazi 69 0 (0.0) 48 (69.6) 12 (17.4) 0 (0.0)
Rwamishenye Kahengere 41 3 (7.3) 5 (12.2) 15 (36.6) 2 (4.9)
Total 488 87 (17.8) 182 (37.3) 113 (23.2) 33 (6.8)

Table 3.

Prevalence of helminths in stool and urine samples among adult population in selected localities in Mwanza region

District Locality Helminth eggs in stool
S. haematobium eggs in urine
No. exam. S. mansoni
Hookworms
No. exam. No. posit. (%)
No. posit. (%) No. posit. (%)
Ilemela Tumaini 14 6 (42.9) 5 (35.7) 14 0 (0.0)
Nyamagana Mazoezi 18 4 (22.2) 0 (0.0) 18 0 (0.0)
Magu Lumeji 37 0 (0.0) 8 (21.6) 37 0 (0.0)
Magu Nyamikoma 50 21 (42.0) 5 (10.0) 50 0 (0.0)
Kwimba Mwaging’hi 20 0 (0.0) 10 (50.0) 20 0 (0.0)
Misungwi Kigongo 48 2 (4.2) 0 (0.0) 48 0 (0.0)
Geita Bugogo 46 0 (0.0) 1 (2.2) 18 0 (0.0)
Geita Chibingo 50 0 (0.0) 8 (16.0) 50 1 (2.0)
Geita Kasamwa 45 2 (4.4) 4 (8.9) 50 2 (4.0)
Sengerema Nyakalilo 50 19 (38.0) 0 (0.0) 49 0 (0.0)
Sengerema Bungonya 47 24 (51.1) 1 (2.1) 50 0 (0.0)
Sengerema Busisi 46 11 (23.9) 0 (0.0) 48 0 (0.0)
Total 471 89 (18.9) 42 (8.9) 265 3 (1.1)

Table 4.

Prevalence of schistosomes and soil-transmitted helminths among adult population in Mara region

District Locality Helminth eggs in stool
S. haematobium eggs in urine
No. exam. S. mansoni
Hookworms
No. posit. (%)
No. posit. (%) No. posit. (%)
Tarime Gamasara 43 1 (2.3) 0 (0.0) 3 (7.0)
Tarime Ochuna 48 1 (2.1) 0 (0.0) 1 (2.1)
Rorya Marasibora 44 0 (0.0) 0 (0.0) 3 (6.8)
Rorya Minigo 44 2 (4.5) 1 (2.4) 8 (18.2)
Musoma Urban Mwisenge 51 7 (13.7) 2 (3.9) 2 (3.9)
Bunda Guta “A” 39 3 (7.7) 0 (0.0) 2 (5.1)
Bunda Nyamitwebili 44 8 (18.2) 0 (0.0) 3 (6.8)
Bunda Bulamba 31 1 (3.2) 0 (0.0) 0 (0.0)
Total 344 23 (6.7) 3 (0.9) 22 (6.4)

Table 5.

Prevalence of parasites among adult population in various localities in Shinyanga region

District Locality Helminth eggs in stool
No. exam. Hookworms (%)
Kahama Mseki 15 5 (33.3)
Kahama Bukomela 47 19 (40.4)
Bukombe Masumbwe 49 6 (12.2)
Shinyanga Rural Luhumbo 31 0 (0.0)
Kishapu Songwa 49 0 (0.0)
Maswa Shishiyu 50 2 (4.0)
Meatu Ngugunu 23 0 (0.0)
Bariadi Sapiwi 39 1 (2.6)
Total 303 33 (10.9)