Figures
Abstract
Background
Sri Lanka, an island located in South Asia, once experienced a notable prevalence of human intestinal nematode infections (HINIs). With the implementation of control programs, infection prevalence was reduced. Detailed information on prevalence, distribution and temporal trends of HINIs is limited. This review aims to explore Sri Lanka’s HINI distribution, trends, diagnostics, control and challenges.
Methodology
We reviewed published information on HINIs in Sri Lanka in electronic databases, local journals and grey literature from inception to September 2022. Based on the Preferred Reporting Items for Systematic Reviews and Meta-Analyses extension for Scoping Reviews (PRISMA-Scr), a systematic strategy was used for searching, screening, reviewing and data extraction. The screening was initiated with a review of titles and abstracts using specific keywords, followed by a full-text screening based on predefined eligibility criteria. A total of 105 studies were included in the review, with 28 selected for pooled prevalence analysis.
Principal findings
The first nationwide survey in 1924 reported a hookworm infection prevalence of 93.1%. By 2017, soil-transmitted helminth (STH) infection prevalence across the island was 0.97% (ascariasis-0.45%, trichuriasis-0.25%, and hookworm infection-0.29%), and the enterobiasis prevalence between 2003 and 2017 ranged from 0% to 42.5%. Strongyloidiasis had been understudied, with a prevalence of 0.1% to 2%. Over the past two decades, the islandwide pooled HINI prevalence was 13.3%. Within specific demographics, it was 6.96% in the general community, 33.4% in plantation sector, and 11.6% in slum communities. During the colonial period, hookworm infection was the commonest HINI, but ascariasis is now more prevalent. The prevailing data relied solely on microscopy, often utilising single stool smears. Mass deworming programs were widely pursued in the first half of the 20th century, initially targeting antenatal women and schoolchildren, and now focusing on specific community groups. National surveys continue monitoring the three main STH infections.
Conclusions
The significant reduction in STH prevalence in the country over the past ten decades highlights the effectiveness of public health interventions, particularly mass deworming programs. Despite the success, STH prevalence disparities persist in vulnerable populations like plantation and slum communities, where hygiene and living conditions continue to pose challenges. Reliance on single stool smear microscopy highlights the need for more sensitive diagnostics to better assess infections. Fluctuating enterobiasis prevalence and limited strongyloidiasis data underscore the importance of continued surveillance and targeted interventions for sustained control and eventual elimination. Sri Lanka’s experiences and control measures offer valuable insights for low-income countries in South Asia and beyond, particularly in managing HINIs with limited resources.
Author summary
Human intestinal nematode infections (HINIs) pose a significant public health concern in Sri Lanka, especially among the deprived communities. Most Sri Lankan research information on HINIs over the years has been scattered and inconsistent, and many are not accessible to all. To address this issue, we conducted an extensive review of the literature from inception to September 2022. The review showed the first HINI to be recorded as hookworm infection, while all five HINI species were reported in Sri Lanka. In the early 1900s infection prevalence was over 90%, and a gradual decline in prevalence over the period was noted. Among the many measures taken to reduce the infection rates since the early part of the 20th century are the national deworming guidelines framed and implemented from 2012 onwards. The current islandwide prevalence of soil-transmitted helminth (STH) infection is less than 1%. Prevalence data on enterobiasis and strongyloidiasis are sparse and the current islandwide prevalence of these two species is not known. As all prevalence estimates were made using microscopic techniques, more sensitive diagnostic methods should be employed to understand the true picture of present low prevalence estimates. The burden of disease is highest in the hill country plantation sector and urban slum communities where living conditions and sanitary facilities are poor. The experiences and control measures implemented in Sri Lanka can offer valuable insights to other countries especially when facing limited resources and similar challenges.
Citation: Jayakody NK, Silva A, Wickramasinghe S, de Silva N, Siribaddana S, Weerakoon KG (2024) Human intestinal nematode infections in Sri Lanka: A scoping review. PLoS Negl Trop Dis 18(12): e0012689. https://doi.org/10.1371/journal.pntd.0012689
Editor: Timir Tripathi, North-Eastern Hill University, INDIA
Received: April 16, 2024; Accepted: November 8, 2024; Published: December 2, 2024
Copyright: © 2024 Jayakody et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: All the data included in the review is provided within the manuscript and in supporting information.
Funding: This review is part of an intestinal parasitoses community evaluation project funded by the National Research Council of Sri Lanka, grant NRC 20-118 to KGW. https://www.nrc.gov.lk. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Introduction
Human intestinal nematode infections (HINIs) are caused by parasitic worms that inhabit the human digestive tract. Disadvantaged communities who live in the tropics and subtropics are more susceptible to their infections [1]. Among these nematodes, Ascaris lumbricoides (roundworm), Strongyloides stercoralis (threadworm), Necator americanus, and Ancylostoma duodenale (hookworm) have complicated life cycles compared to those of Enterobius vermicularis (pinworm) and Trichuris trichiura (whipworm). While S. stercoralis and E. vermicularis can spread directly from person to person, others, like A. lumbricoides, T. trichiura, N. americanus, and A. duodenale, need a mandatory soil phase to mature, hence named soil-transmitted helminth (STH) or geohelminths [2]. HINIs are transmitted either by ingestion of eggs or by infective larvae penetrating the bare skin [2]. In the majority, they cause a wide range of non-specific illnesses [3]. Heavy infections are linked to impaired physical and intellectual development, anaemia, and reduced resistance to invading microbes [3]. Children, expectant mothers, farmers and plantation labourers are the groups most at risk of contracting HINIs [4]. The physiological demands for nutrients for growth and development in children and pregnant women make them more susceptible to complications associated with these diseases [4]. As the infections are linked to inadequate access to safe water, low socioeconomic standards, poor personal hygiene and poor sanitation practices, wearing footwear and gloves in outdoor activities, improving the quality of water, sanitation and hygiene (WASH) can be used as effective prevention and control strategies [5]. Periodic mass anthelminthic medication delivery through school-based programmes and clinics is another control measure [2,6,7].
Globally, over 1.5 billion individuals suffer from STH infections [4]. As of the current global situation, approximately 807–1121 million people are infected with roundworms, 604–795 million with whipworms, 576–740 million with hookworms, 200 million with pinworms, and 600 million with threadworms [4,8,9]. Polyparasitism is common in high-endemic areas [10]. In 2012, the World Health Organization (WHO) identified STH infections as the most common neglected tropical disease (NTD) in their roadmap to combat NTDs [11]. This increased awareness helped in achieving many control and preventive goals of the disease. The maximum rates of HINIs are found in Sub-Saharan Africa, East Asia, China and the Americas [4].
Asia is responsible for 67% of the world’s prevalence of STH infections [12–14]. India has the highest reported prevalence of STH infections in South Asia, which is 21% [15]. With an overall prevalence of 18%, A. lumbricoides was the most common species of STH in South and Southeast Asia, followed by T. trichiura (14%) and hookworm (12%) [16]. However, the overall prevalence of STH infections is decreasing throughout Asia [17].
A. lumbricoides, N. americanus and T. trichiura have been identified as the three main STHs in Sri Lanka since the past century [18]. In Sri Lanka, systematic antenatal mebendazole deworming was introduced in the 1980s. Deworming was integrated into school health programs in 1960 [19]. The islandwide cumulative STH prevalence in Sri Lanka is 0.97% in 2017 [20].
In this review, scattered information on HINIs in Sri Lanka was arranged in a sequential order to understand trends of infection with past and current infection prevalences, identify the isolated pockets with high endemicity, and interventions made. Such information has the potential to direct responsible bodies, both locally and globally, to focus their management efforts on highly endemic areas and needy communities when available resources are limited. The findings of this review would assist in planning future research and guide health sector authorities to strategically address the control and prevention of HINIs in a manner that is both cost-effective and targeted.
History of the disease in Sri Lanka
Sri Lanka was made a Crown colony (Ceylon) in 1815 [21]. British landowners employed labourers from India to fill the labour deficit in the plantation industry. In 1888, HINIs were first recorded in the annual survey of the Principal Civil Medical Officer (PCMO) of Sri Lanka, when 31 individuals with hookworm infection were discovered [22]. All the diagnosed people were immigrant workers. Hookworm disease was responsible for 269 fatalities by 1897 [22]. The employees were exposed to a diverse spectrum of infections and parasitic illnesses particularly due to the severely unhygienic conditions that prevailed on the plantations [23]. Registrar General of Ceylon’s annual report in 1891 noted that the disease had been introduced to the island by the Indian Malabar coolies [23]. By 1916, the disease had affected over 90% of the people living in the estates [21]. A hookworm control programme was started in 1916 by the International Health Board (IHB) of the Rockefeller Foundation in the Matale area, which was home to roughly around 10,000 South Indian immigrant workers [21].
Social and geo-climatic profile of Sri Lanka
Sri Lanka is a South Asian country with a tropical climate. It is located between 5° 55’ and 9° 51’ north latitude and 79° 42’ and 81° 53’ east longitude [24]. In the driest regions (northern, northwestern, and southeastern), the mean annual rainfall is less than 900mm, whereas, in the wettest regions (western slopes of the central highlands), it exceeds 5000mm [24,25]. The mean annual temperature in the central highlands, is around 16°C (1900m above mean sea level), while it is around 27°C in the coastal lowlands [24]. The country is geographically divided into three major ecological zones: wet, arid and dry [24,25]. There are nine provinces, Northern (NP), North Central (NCP), North Western (NWP), Eastern (EP), Uva (UP), Central (CP), Southern (SP), Sabaragamuwa (SBP) and Western (WP), and 25 districts. Districts are second-level administrative divisions, while provinces are at the apex level. The population of Sri Lanka was 22.16 million in 2021 [26]. The estimated gross domestic product per person was dollar 3292 in 2022 [26]. About 25.2% of people were estimated to be poor in 2022 [27]. Of the population, 98.2%, 87.6%, and 18.9% are enrolled in primary, secondary, and tertiary education, respectively [28]. The adult literacy rate was 92.3% in 2019 [26]. According to the Demographic Health Survey 2006 and 2020, Sri Lanka has increased access to safe drinking water from 76% to 93.2% [26].
Methods
This scoping review was developed following the methodological framework proposed by Arksey and O’Malley in 2005 [29], which has been further developed by Levac et al. [30] and the Joanna Briggs Institute (JBI) [31,32]. Accordingly, the review proceeds through the following five steps; Identifying the review question, Identifying relevant studies, Study selection, Charting the data, Collating, summarising and reporting the results. To enhance the methodological rigour and reporting quality of this scoping review, the Preferred Reporting Items for Systematic Reviews and Meta-Analyses extension for Scoping Reviews (PRISMA-ScR) checklist (S1 PRISMA checklist), was also followed [33].
Identifying the review question
Following an exploratory review of the literature on HINIs in Sri Lanka, the following questions were identified.
- Details of the studies conducted in Sri Lanka on HINIs; the number of studies, research area explored and extent of the research.
- For the past two decades, HINI prevalence, geographical location, trends of the infection, the impact of control programmes on the prevalence and delimitations.
- Research gaps in understanding HINIs in the Sri Lankan context.
We used the population, concept, and context (PCC) format to align the study selection with the research question.
Identifying relevant studies
A comprehensive search of PubMed, Google Scholar, CINAHL, Trip, Oxford Journal, Taylor & Francis Online, JSTOR, Emerald Insight, Scopus, Cochrane Library and Science Direct databases was carried out independently by NKJ and KGW using the Search:(((((((((((((((("ascaris"[All Fields]) OR ("roundworm"[All Fields])) OR ("necator"[All Fields])) OR ("ancylostoma"[All Fields])) OR ("hookworm"[All Fields])) OR ("strongyloides"[All Fields])) OR ("threadworm"[All Fields])) OR ("trichuris"[All Fields])) OR ("whipworm"[All Fields])) OR ("enterobius"[All Fields])) OR ("pinworm"[All Fields])) OR ("soil transmitted helminth"[All Fields])) OR ("intestinal nematodes"[All Fields])) OR ("geohelminth"[All Fields])) OR ("helminth"[All Fields]))) AND ((("sri lanka"[All Fields]) OR ("ceylon"[All Fields])) OR ("srilanka"[All Fields])). Studies published from inception to September 2022 were reviewed with no language restrictions. Duplicates were removed with the Rayyan software [34]. Local journals, Sri Lankan institutional repositories and administrative archives were also searched electronically and manually. The bibliographies, Medical publications relating to Sri Lanka 1811–1976,1981–1988 [35,36], Health in Sri Lanka 1977–1980 [37], Medical literature 1980–2005 and dissertations and theses presented to the Post Graduate Institute of Medicine, Sri Lanka were also searched. Reference lists of all relevant studies were evaluated for additional articles.
Study selection
Selected articles from the electronic database search and the hand search of the published literature were transferred to 2022 Rayyan (https://www.rayyan.ai) [34], from which duplicates were removed. Two reviewers (NKJ and KGW) independently screened the selected articles, initially for the title and abstract against the eligibility criteria. All the articles with discrepancies were included for full-text screening. Full-text screening of the selected articles was done by the same reviewers independently. Issues arising from the full-text screening were addressed by a third reviewer (NDS) with joint discussions involving NKJ and KGW. Reasons for the exclusion of any full-text source of evidence are reported. The methodology is illustrated in the PRISMA flowchart (Fig 1).
The selection of eligible studies was guided by the PCC framework.
Inclusion criteria
- Qualitative and quantitative studies containing data on prevalence, clinical presentation, risk factors, diagnostic approaches, treatment, control programmes, and drug efficacy on HINIs in Sri Lanka.
- Grey literature including primary research studies, conference abstracts, bibliographies, government reports and guidelines.
- Reviews, reports, commentaries and editorial articles that address the objectives of this scoping review.
- There were no language restrictions.
- Studies published up to September 2022 from inception were included, as the final search of the literature was carried out in September 2022.
Exclusion criteria
- Studies carried out on the Sri Lankan communities residing in other countries. (As they are not exposed to the same climatic, socioeconomic, WASH conditions as Sri Lankan residents)
- Case reports and case series.
- Veterinary studies.
Charting the data and quality assessment
The data extraction form was developed in Microsoft Excel using the JBI data extraction instrument as a guide [39]. Two reviewers (NKJ and KGW) used the customised data extraction form to retrieve information independently. The data extraction process was validated on the first ten articles to ensure consistency. The data of the remaining articles were extracted by a single reviewer (NKJ). Questions during data extraction were discussed with KGW and NDS. Data extracted falls into the following domains: publication details, study methodology, study setting, participant information (age, sex, cultural details if available), parasite species, diagnostic methods, treatments, and control programs carried out, prevalence, intensities of infection, strengths and limitations of the studies. In drug efficacy studies, the name of the drug, dose, dosage, total egg clearance rate (ECR) and egg reduction rate (ERR) were extracted. Extracted data is presented in a summary form ensuring that the objectives of the review are achieved.
Newcastle-Ottawa Quality Assessment (NOQA) Scale modified for cross-sectional studies [40] was utilised to assess the quality of the epidemiological studies for the last two decades (S1 Table). Two reviewers (NKJ and KGW) independently evaluated the quality of the studies and discrepancies that occurred during the process were resolved by the opinion of a third reviewer (NDS). NOQA includes quality assessments in three domains: selection, comparability and outcome. The NOQA tool has scores ranging from 0 to 10. Studies with scores less than 4 were defined as unsatisfactory, 5–6 as satisfactory, 7–8 as good and 9–10 as very good.
Results
Studies under review
After the full-text screening, 105 articles were included in the review. All the publications were in the English language. Over 75% (n = 89, 84.7%) of the articles were published since 1975 (Fig 2A). The majority of studies 47 (44.8%) had an epidemiological focus. Others were on drug efficacy, history of the disease, clinical features, diagnosis, treatment, knowledge and associated factors, general reviews, short reports and deworming guidelines (Fig 2B).
(A) Sri Lankan publication productivity on HINIs (B) Number of articles according to their scope. KAP, knowledge, attitude and practices.
Studies on the efficacy and effectiveness of anthelmintic drugs
Fifteen studies have focused on HINI treatment efficacy and effectiveness (Table 1). The effectiveness of a drug relates to its performance in practical application, contrasting with efficacy, which measures its performance in randomised controlled trials (RCTs) or laboratory studies. In Sri Lanka, all the drug efficacy studies were carried out as RCTs. Parasite detection in pre and post-treatment stool samples was accomplished using direct wet smear (DWS) (50%), Stoll’s egg counting (16.6%), Kato-Katz (KK) (33.3%), merthiolate iodine formaldehyde concentration (MIFC) (8.3%), flotation technique (8.3%) and Scotch tape method (8.3%). Two studies have used more than one diagnostic technique for the detection of ova. The efficacy of ten different medications was evaluated in these trials by ECR and ERR. The percentage of individuals who turned stool-negative after treatment is defined as ECR, and the percentage reduction of the mean post-treatment egg count compared to the mean pre-treatment egg count is defined as ERR [41]. Bephenium hydroxynaphthoate (BH), pyrantel pamoate (PP), and tetrachlorethylene (TCE) were effective in treating HINIs [42]. Three daily doses of BH or PP had comparable effects to a single dose of TCE, though both BH and PP are inferior to TCE in a single dose [42–44]. Mebendazole and albendazole are both effective against HINIs, with mebendazole more successful against whipworm and albendazole against hookworm infestations [45–47]. Mebendazole is recommended for multiple infections, especially with whipworm [48], while albendazole is preferred for hookworm-related complications [47]. As mebendazole is cheaper than albendazole, it was recommended for mass drug administration (MDA). Multiple-dose mebendazole regimens are more effective, particularly in its polymorph C form [49,50]. Flubendazole, piperazine, pyrantel and oxantel are effective against ascariasis but less so against trichuriasis [51–53]. Albendazole with diethylcarbamazine (DEC) or alone shows comparable efficacy, while albendazole combined with ivermectin is highly effective against trichuriasis [54,55]. Early trials primarily investigated the effectiveness of BH, TCE, pyrantel, and oxantel, whereas recent studies have shown that albendazole and mebendazole exhibit efficacy in treating HINIs (Table 1).
Studies with an epidemiological focus
Of the 47 epidemiological studies, 4 (9%) were islandwide surveys and 43 (91%) were district and provincial-level prevalence assessment studies. Islandwide surveys were conducted in the years 1924, 1937, 2003, and 2017 (Fig 3) involving primary schoolchildren. Province-level prevalence assessment studies were distributed among seven provinces (Fig 4A) and no individual studies were conducted in NWP and NCP. WP was the most assessed province with 15 (34.8%) studies conducted. (Fig 4A). Four studies were conducted concurrently involving several provinces, with two studies focusing on both the WP and SBP, another involving SBP and the CP, and a third in SBP, UP, and the CP. The majority of the epidemiological studies (n = 45, 95.7%) were conducted in community settings while only 2 (4.3%) were hospital-based (Fig 4C). The most sought communities were the general community (n = 21, 46.6%), plantation sector (n = 14, 31.1%) and slum communities (n = 7, 15.5%). Other studies focused on some special communities like indigenous, displaced residing in refugee camps, and inmates of psychiatric institutions. The majority (80.9%) of the studies were conducted among schoolchildren (Fig 4C). Studies have used different diagnostic methods like DWS, KK, MIFC, formalin ether concentration techniques (FECT), Stoll’s egg counting method, culture methods, flotation methods and Scotch tape method. Some studies have used multiple diagnostic methods (Fig 4C). Three STH infections ascariasis, trichuriasis and hookworm infection prevalence were extensively assessed, with 40 (85.1%) on ascariasis, 40 (85.1%) on hookworm infections, and 37 (78.7%) on trichuriasis. Enterobiasis and strongyloidiasis were less frequently assessed with 13 (27.6%), and 8 (17.0%) focusing on their prevalence respectively. Some studies provided prevalence figures for all HINIs, whereas others only provided values for one or two species (Fig 4B).
Demarcations within the country are the provincial boundaries. Prevalence value for each province is given. NP, Northern Province; NCP, North Central Province; CP, Central Province; NWP, North Western Province; EP, Eastern Province; UP, Uva Province; SBP, Sabaragamuwa Province; WP, Western Province; SP, Southern Province. (The base layer of the map was sourced from d-maps.com:free maps. https://d-maps.com/carte.php?num_car=56323&lang=en).
(A) Province-wide distribution of epidemiological studies. Demarcations within the country are the provincial boundaries and the values indicate the number of epidemiological studies carried out in each province. (B) Venn diagram showing different types of human intestinal nematodes assessed in epidemiological studies. (C) Number of epidemiological studies conducted according to their setting, population and diagnostic methods used. DWS, direct wet smear; MIFC, merthiolate iodine formaldehyde concentration; FECT, formalin ether concentration technique; KK, Kato-Katz. (The base layer of the map was sourced from d-maps.com:free maps. https://d-maps.com/carte.php?num_car=56323&lang=en).
Prevalence and communities affected
The review revealed that HINIs were widely dispersed in Sri Lanka before the year 2000 but gradually declined thereafter. Infections were documented in nearly every geographical and ecological region of the island. During the colonial regime, the highest prevalence rate (98.1%) was reported from the Matale district of the CP [57]. As of today, the Nuwara-Eliya district in the central highlands and the Colombo district in the western lowlands are the most endemic areas for HINIs, with roundworms being the most commonly reported [20].
For the last two decades, twenty-eight prevalence assessment studies have been conducted employing copromicroscopic methods (Table 2). All of them were descriptive cross-sectional studies or national surveys with a minimum sample size of 103 in NP and an islandwide survey having the highest sample size of 5500 [58]. Many studies have focused on WP and CP. Studies show that HINIs are seen among all age groups involving different communities. The majority (n = 24, 85.7%) of studies have assessed the prevalence of at least one of the three main STH infections (ascariasis, trichuriasis, and hookworm infection).
We included twenty-eight prevalence assessment studies conducted over the past two decades for the pooled prevalence assessment (Fig 5). Among a total of 16407 children who participated, involving all the community groups; 2186 were infected with at least one of the three HINIs (Ascaris, Trichuris, and hookworm), yielding a pooled prevalence of 13.3% (95% CI 12.7–28.9). Of the participants, 1664, 393, and 580 were positive for ascariasis, trichuriasis, and hookworm infections with a pooled prevalence of 10.1% (95% CI 7.6–24.6), 2.4% (95% CI 0.7–5.1) and 3.5% (95% CI 0.1–7.7) respectively.
N, number of studies; STH, soil-transmitted helminths.
For the enterobiasis prevalence assessment, 2132 children participated. Of the participants, 698 were positive for enterobiasis giving a pooled prevalence of 32.73% (95% CI 13.77–45.67). Not enough data was available to assess the pooled prevalence of enterobiasis for each population category.
In general community studies involving 11,850 participants, 852 were found positive for at least one STH, resulting in an overall prevalence of 6.96% (95% CI 3.5–30.9). The pooled prevalence rates for ascariasis, trichuriasis, and hookworm infestation were 4.9% (95% CI 1.7–12.3), 1.91% (95% CI 0.4–7.7), and 0.80% (95% CI 0.4–2.7), respectively (Fig 6).
STHs, soil-transmitted helminths.
Within the plantation sector community comprising 4,351 children, 1,453 were identified as positive for at least one type of STH infection, resulting in a pooled prevalence of 33.4% (95% CI 26.1–35.1). The pooled prevalence rates for Ascasis, Trichuris, and hookworm infections were 25.3% (95% CI 21.3–34.5), 4.9% (95% CI 1.1–5.96), and 5.7% (95% CI 1.6–8.3), respectively. Only one study was conducted in the slum community involving 206 children with a cumulative STH prevalence of 11.6% and Ascaris, Trichuris and hookworm infection prevalence at 9.7%, 1% and 1% respectively (Fig 6). Pooled prevalence assessments for special community groups, such as indigenous and displaced populations, were not conducted due to the limited availability of studies, with only a single study had been performed among these communities.
When examining, several studies did not report on infection intensity. Among the studies that reported infection intensity, the methods of intensity classification were inconsistent, while some reported the mean egg per gram (EPG) count for each species, and others categorised intensity into varying levels such as light, moderate, and heavy, light versus moderate to heavy and light, moderate to heavy and heavy. Due to these inconsistencies and the lack of comprehensive data, we were unable to conduct a thorough assessment of the prevalence of different infection intensities.
The trends of reported infections
Throughout the review period, a general downward trend in infection prevalence of STHs was observed across all communities studied. However, certain communities, notably those in the plantation sector and slums, continue to exhibit higher prevalence rates compared to the general population. According to the latest national survey, conducted in 2017, the cumulative STH prevalence was recorded at 0.97% for the general community, 2.7% for slum areas, and 9.02% for plantation communities [20]. Despite the overall decline in STH infection prevalence, studies assessing Enterobius infection consistently revealed high prevalence rates ranging from 30% to 40% [76]. Even the most recent study conducted in 2017 reported a prevalence of 42% [78]. Conversely, Strongyloides infections have shown consistently low prevalence rates throughout the review period, with three consecutive studies reporting 0% prevalence. Additionally, prevalence values obtained from special communities such as indigenous (23%), refugees (21%) and inmates of psychiatric institutions (46%) consistently indicate higher trends compared to the general community [63,69,84]. This highlights the importance of targeted interventions and tailored public health strategies to address the specific needs of these vulnerable populations.
Sri Lanka maintained a biannual deworming program targeting school children in the plantation sector from 1994 to 2005 due to an initial STH prevalence of 90% [18]. This was abandoned due to lack of funding and in 2009 study done in the same area showed an increase in prevalence from 19% in 2005 to 29% [66,72]. The study highlights that without sustained preventive measures, infection rates can rebound, emphasising the need for ongoing interventions.
Factors associated with transmission
Studies have shown that the prevalence of HINIs in any area is determined by factors such as temperature, rainfall, soil, vegetation, drainage, irrigation, coprophagy of domestic animals, sanitation, occupation, and the habits and customs of the people [57]. A plantation industry survey showed that 50.0% of the participants were excreting Ascaris eggs [85]. Only 30.7% of the respondents had access to latrines, and nearly all (96.6%) lived in terraces of one-room dwellings, showing that unsanitary living circumstances and subpar sanitation facilities increase the spread of infection [85]. Geohelminthic infection prevalence was high among a community living in an area where soil contamination was high with geohelminthic eggs [86]. The use of unprotected wells, the absence of water-sealed latrines, and bathing and washing in rock pools created by waterfalls all greatly increase the likelihood of hookworm infections [63]. Poor environmental sanitation, inadequate personal hygiene, limited toilet facilities, unplanned home garden cultivation, and poverty were found to be variables contributing to the prevalence of HINIs in the communities. Over time, improvements in sanitary facilities in the country may have had a favourable impact on the decline in HINI prevalence. All KAP surveys showed that knowledge among participants was poor [86–88]. This could be a reason that some of the communities continue to have relatively high levels of HINI prevalence despite the control measures.
Preventive and control measures
Population growth in Sri Lanka necessitated large-scale investment in WASH. Between 2015 and 2019, there was a notable increase in budgetary expenditure for WASH, reaching the Sri Lankan rupee (LKR) 49.5 billion in 2019, reflecting the economic development and the government’s growing commitment [89]. However, during the COVID-19 pandemic, the emphasis on sanitation increased, diverting attention from other disease control measures. Even though 90% of households have access to safe drinking water and sanitation, strong spatial differences exist with only 36% having access to piped water and 2% to piped sewerage [89]. Coverage is more in urban areas with 99.9% of the population in Colombo having access to clean water while it is 54% in Nuwara Eliya where many of the plantation sector communities reside with high levels of HINIs reported [90]. Sri Lanka aims to provide universal access to safe water by 2025, sanitation by 2030 and end open defecation by 2025 [89]. To bridge decades of uneven progress with improved access to water and sanitation and to achieve the above targets the country needs a well-planned government policy [91]. Sri Lanka has undertaken several completed and ongoing projects, including the Gift Water Project, Access to Water for Communities Affected by Drought (AWCAD) Project, Water & Sanitation in Schools and Communities (WSSC) Project and WASH-TE II Project, to contribute towards these aims [92]. Government and health authorities have taken continuous steps with medications to improve and maintain a low infection prevalence in the country.
In the early 20th century, Sri Lanka pursued mass deworming programs. From 1994 to 2005, a biannual program targeting school-aged children with mebendazole addressed the high prevalence of STH infections [18]. However, after its cessation due to funding issues, a 2009 study showed a high overall prevalence of STH infections (29.0%) in estate sector schools, indicating a rebound effect [18]. For the first time in 2012, the Family Health Bureau (FHB) of Sri Lanka’s Ministry of Health issued guidelines for community-based deworming of children and pregnant women [18]. These guidelines categorised regions into high-risk, moderate-risk and low-risk areas, based on national surveys. They recommended biannual deworming with mebendazole for children in high-risk areas and annual deworming for those in moderate-risk regions [93]. Pregnant women were also included in the program due to the adverse effects of hookworm infections, particularly on iron deficiency anaemia [93]. The national survey done in 2017 showed a decline in the overall prevalence of STH infections across the country, prompting the FHB to revise the deworming guidelines issued by the Ministry of Health by discontinuing deworming in low-risk areas and tailing down the deworming in other areas.
Regional comparisons
When comparing Sri Lanka’s HINI situation with other countries, notable differences and similarities emerge. India has the highest microscopic prevalence of STH infections in South Asia, which is 21% (13). With an overall prevalence of 18%, Ascaris was the most common species in South Asia, followed by Trichuris (14%) and hookworm (12%) (13). Bangladesh showed a notable reduction in STH prevalence from 79.8% in 2005 to 14% in 2020, attributed to the introduction of the MDA program in 2008 [94]. China successfully reduced STH prevalence from 53.58% in 1988–1992 to 0.84% in 2020 [95]. Countries with robust healthcare systems and extensive deworming programs, such as Singapore and Japan, have successfully maintained low STH prevalence levels [90]. Similarly, in Africa, countries like Ethiopia and Nigeria face challenges akin to economic instability and limited access to healthcare exacerbating STH prevalence [96,97]. Studies conducted in Myanmar reveal that while the microscopic prevalence of STH is 33.3%, the molecular prevalence is significantly higher at 78% [98]. There was no comprehensive data on the molecular prevalence of HINIs for many countries, except for some regions. For example, in Vietnam, molecular studies have revealed the unequal distribution of STH infection among different areas implying the STH control programmes may not be reaching certain areas. However, more research is needed to fully understand the molecular epidemiology of STH infections in these countries and its impact on control efforts.
One of the problems with STH prevalence assessment studies in Asia is the broader variety of diagnostic techniques utilised making it challenging to compare the outcomes directly [13]. Many countries have implemented regular deworming programs, resulting in reduced prevalence of STH infections. However, certain regions within these countries continue to experience high prevalence rates due to dense populations and inadequate sanitation facilities. While most nations conduct mass deworming initiatives targeting schoolchildren, some have extended these efforts to include adults [99]. Integrated control programs, such as the anti-filarial and deworming program in Sri Lanka and the African Programme for Onchocerciasis Control (APOC), demonstrate the efficacy of collaborative approaches in reducing government costs associated with deworming [99]. Regional collaborations, such as the East Asia Summit (EAS) and the Association of Southeast Asian Nations (ASEAN), provide platforms for sharing experiences and best practices in STH control, facilitating efforts to reduce the burden of STH infections across Asia [100]. These comparisons underscore the importance of contextual factors, healthcare infrastructure, and collaborative strategies in addressing the complexity of STH infections.
Discussion
For the first time, the current study presents an in-depth account of the trends of infection, current prevalence, associated factors, diagnostic methods, prevention and control strategies of HINIs in Sri Lanka. This scoping review is timely, coinciding with Sri Lanka’s achievement of a prevalence of less than 1% for STH and cessation of regular deworming in three districts, in alignment with the WHO’s strategy to eliminate STH by 2030 and reduce the required number of tablets in preventive chemotherapy [20]. Over the past 20 years, the STH prevalence in Sri Lanka remained low and continued to decline gradually reaching 0.97% in 2017 [7,20] Throughout the period, slum communities and plantation sector communities showed a higher prevalence of HINIs compared to the general community remaining at 2.73% and 9.02% respectively in 2017 [20]. This can be attributed to the socioeconomic disparities, crowded living conditions and low education levels seen in these areas compared to other regions of the country [89]. The implementation, continuation and monitoring of regular school-based deworming programmes positively impacted the control of infection in Sri Lanka [93].
There is a notable gap in research from regions like NWP, NCP, EP, SBP, SP and NP, especially in recent years and at-risk populations with frequent soil exposure occupations. Less attention was given to studying intestinal nematodes like E. vermicularis and S. stercoralis. The WHO 2021–2030 roadmap for neglected tropical diseases (NTDs) recommends establishing an effective strongyloidiasis control program for school-age children [101]. However, in the Sri Lankan context, it is crucial to first have a comprehensive understanding of the prevalence of strongyloidiasis within the community through extensive surveillance efforts. Prevalence assessment studies have not incorporated molecular methods, which offer greater sensitivity, particularly considering the low infection intensity prevalent in the country. This could potentially be due to the high initial costs, maintenance challenges, scarcity of skilled personnel, infrastructure limitations, inconsistent supply chains, and expensive consumables, which pose significant challenges in a resource-limited setting like Sri Lanka [102,103]. Moreover, many studies rely on single stool samples for analysis and non-gold standard techniques such as DWS, FECT, and KK were used to assess strongyloidiasis and enterobiasis prevalence. These factors collectively contribute to the likelihood of underreporting HINI prevalence.
Incorporating enterobiasis prevalence assessment into the national survey would be beneficial, given its high prevalence in conducted studies. This inclusion could lead to more effective control strategies. KAP surveys highlight low awareness and misconceptions regarding symptoms, transmission, prevention, and deworming [88]. Therefore, prioritising health promotion programs to enhance knowledge and improve attitudes and practices is crucial. Furthermore, addressing overcrowding and inadequate infrastructure facilities in slum and plantation sector communities should be a government priority at all administrative levels to effectively control these issues. As the last national survey gives recommendations up to 2022, conducting another survey is important, especially in regions where deworming was discontinued. Molecular prevalence assessment will benefit in accurately identifying HINI prevalence in the country.
This study has several limitations. An in-depth analysis of the prevalence was difficult as most of the studies were without adequate methodological detail with regard to the subjects and the diagnostic techniques. For example, a broader variety of diagnostic techniques utilised, such as DWS, FECT, KK and salt flotation techniques with different sensitivities and specificities prevents a reasonable comparison of the outcomes. As this scoping review aims to explore Sri Lanka’s HINI history, distribution, trends, control, diagnostics, and challenges, we avoided constraining the time frame, or specific publication types except for case reports, nor did we limit studies based on stringent methodological criteria. Consequently, encompassing a broader timeframe and, period incorporating much grey literature lacking in methodological detail rendered, a thorough meaningful analysis of the quality of evidence provided by the publications was unfeasible. We only assessed the methodological quality of the prevalence assessment studies incorporated for the pooled prevalence analysis.
As HINIs are endemic in many regions worldwide, lessons learned from Sri Lanka’s experiences can inform policy decisions and intervention strategies in other countries facing similar challenges. The identification of regional disparities and the evaluation of control strategies offer actionable insights for policymakers and public health practitioners working to achieve targets set forth by organisations. By fostering collaboration among researchers, policymakers, healthcare providers, and community stakeholders, this review shows the multisectoral approach necessary for achieving sustainable improvements in public health outcomes worldwide. By advocating for equitable access to healthcare, education, and socioeconomic opportunities, stakeholders can address the underlying determinants of HINIs and other NTDs, ultimately working towards health equity on a global scale. In summary, this scoping review on HINIs in Sri Lanka not only contributes valuable insights to the national context but also holds significant implications for global health. By informing policies, advancing research agendas, fostering collaboration, and advocating for equity, this review contributes to the collective effort to eliminate NTDs and improve health outcomes for populations worldwide.
Conclusion
The efforts to eliminate HINIs in Sri Lanka have led to the classification of certain districts as low, moderate, or high risk in line with the WHO risk classification. Despite numerous studies conducted in some districts and communities, we observed a low number of published research on HINIs in general and a persistent vulnerability among slum and plantation communities. Children, pregnant women, slum dwellers, and plantation workers remain most susceptible, with roundworm and hookworm being the most prevalent infections. While prevalence has generally declined, strict comparisons between studies are hindered by methodological differences. Sri Lanka’s successful control programs offer valuable lessons for other countries in the region as well as across the globe, emphasising comprehensive approaches including health education, sanitation, treatment, and community engagement. Adaptation to local contexts is key to success in combating these infections worldwide.
Supporting information
S1 PRISMA Checklist. PRISMA-ScR checklist.
Preferred Reporting Items for Systematic reviews and Meta-Analyses extension for Scoping Reviews Checklist.
https://doi.org/10.1371/journal.pntd.0012689.s001
(PDF)
S1 Table. Quality assessment of epidemiological studies from the year 2000, based on the modified Newcastle-Ottawa Quality Assessment Scale
https://doi.org/10.1371/journal.pntd.0012689.s002
(PDF)
Acknowledgments
We would like to thank Ms Chithra M Abeygunasekera, Senior Assistant Librarian, Faculty of Medicine, University of Kelaniya for her valuable support.
References
- 1.
World Health Organization (WHO) (2010). Working to overcome the global impact of neglected tropical diseases: first WHO report on neglected tropical diseases. World Health Organization. Available from: https://www.who.int/publications/i/item/9789241564090
- 2. Jourdan PM, Lamberton PHL, Fenwick A, Addiss DG. Soil-transmitted helminth infections. Lancet. 2018 Jan 20;391(10117):252–265. Epub 2017 Sep 4. pmid:28882382
- 3. Centers for Disease Control and Prevention (CDC). About soil-transmitted helminths [Internet]. 13 June 2024. [cited 2024 Sep 5]. Available from: https://www.cdc.gov/sth/about/index.html
- 4. World Health Organization (WHO). Soil-transmitted helminth infections. [Internet]. 18 January 2023. [cited 2023 Oct 26]. Available from: https://www.who.int/news-room/fact-sheets/detail/soil-transmitted-helminth-infections
- 5. Strunz EC, Addiss DG, Stocks ME, Ogden S, Utzinger J, et al. Water, sanitation, hygiene, and soil-transmitted helminth infection: a systematic review and meta-analysis. PLoS Medicine 11(3): e1001620. pmid:24667810
- 6. Montresor A, Mupfasoni D, Mikhailov A, Mwinzi P, Lucianez A, et al. (2020) The global progress of soil-transmitted helminthiases control in 2020 and World Health Organization targets for 2030. PLoS Negl Trop Dis. 14(8): e0008505. pmid:32776942
- 7.
World Health Organization (WHO) (2020). Ending the neglect to attain the sustainable development goals a rationale for continued investment in tackling neglected tropical diseases 2021–2030. World Health Organization. Available from: https://www.who.int/publications/i/item/9789240010352
- 8. Centers for Disease Control and Prevention (CDC). Parasites—Soil-transmitted helminths [Internet]. 2 February 2022. [cited 2023 Oct 26]. Available from: https://www.cdc.gov/parasites/sth/index.html
- 9. Kucik CJ, Martin GL, Sortor BV. Common intestinal parasites. Am Fam Physician. 2004 Mar 1;69(5):1161–8. pmid:15023017.
- 10. Howard SC, Donnell CA, Chan MS. Methods for estimation of associations between multiple species parasite infections. Parasitology. 2001;122(Pt 2):233–51. pmid:11272654
- 11.
World Health Organization (WHO) (2012). Accelerating work to overcome the global impact of neglected tropical diseases: a roadmap for implementation: executive summary. World Health Organization. Available from:https://iris.who.int/handle/10665/70809
- 12. Pullan RL, Smith JL, Jasrasaria R, Brooker SJ. Global numbers of infection and disease burden of soil transmitted helminth infections in 2010. Parasit Vectors. 2014 Jan 21;7:37. pmid:24447578
- 13. Dunn JC, Turner HC, Tun A, Anderson RM. Epidemiological surveys of, and research on, soil-transmitted helminths in Southeast Asia: a systematic review. Parasit Vectors. 2016 Jan 27;9:31. pmid:26813007
- 14. Pullan RL, Brooker SJ. The global limits and population at risk of soil-transmitted helminth infections in 2010. Parasit Vectors. 2012 Apr 26;5:81. pmid:22537799
- 15. Ajjampur SSR, Kaliappan SP, Halliday KE, Palanisamy G, et al. (2021) Epidemiology of soil transmitted helminths and risk analysis of hookworm infections in the community: Results from the DeWorm3 Trial in southern India. PLoS Negl Trop Dis. 2021 Apr 30;15(4):e0009338. pmid:33930024
- 16. Silver ZA, Kaliappan SP, Samuel P, Venugopal S, Kang G, Sarkar R, Ajjampur SSR. (2018) Geographical distribution of soil transmitted helminths and the effects of community type in South Asia and South East Asia—A systematic review. PLoS Negl Trop Dis. 2018 Jan 18;12(1):e0006153. pmid:29346440
- 17. Jex AR, Lim YA, Bethony JM, Hotez PJ, Young ND, Gasser RB. (2011) Soil-transmitted helminths of humans in Southeast Asia-Towards integrated control. Adv Parasitol. 2011;74:231–65. pmid:21295679
- 18. De Silva NR. (2018) The soil-transmitted helminths in Sri Lanka: A review of the recent literature. Sri Lankan J Infect Dis. 2018;8(2):60–68.
- 19.
Ministry of Health (MOH). (2012) Guidelines on deworming children and pregnant women in community setting:2013–2016. General circular No. 02–172/2012. Ministry of Health of Sri Lanka.
- 20. Ediriweera DS, Gunawardena S, Gunawardena NK, Iddawela D, Kannathasan S, Murugananthan A, et al. (2019) Reassessment of the prevalence of soil-transmitted helminth infections in Sri Lanka to enable a more focused control programme: a cross-sectional national school survey with spatial modelling. Lancet Glob Heal. 2019;7(9):e1237–46. pmid:31331809
- 21. Hewa S. (1994) The hookworm epidemic on the plantations in colonial Sri Lanka. Med Hist. 1994;38(1):73–90. pmid:8145609
- 22. Archives Registration, (1888) Anchylostomiasis-Ceylon, administration reports, Principal Civil Medical Officer and Inspector General of Hospitals, 1888 (abstracted), RG. 5, Se. 2, Box 47. Regist Arch.
- 23. Archives Registration, 1981 Administration reports, vital statistics: report of the Registrar General of Ceylon. (abstracted), RG. 5, Se. 2, Box 47. Regist Arch.
- 24. Sri Lanka—Climatology | Climate change knowledge portal. [Internet]. 2023. [cited 2023 October 26]. Available at https://climateknowledgeportal.worldbank.org/country/sri-lanka
- 25. Ministry of Environment Sri Lanka. Central Environmental Authority. [Internet]. 2023. [cited 2023 October 26]. Available at http://www.cea.lk/web/en/component/content/article/22-contact-us/154-ministry-of-environment/
- 26. Department of Census and Statistics Sri Lanka. Population [Internet]. 2023. [cited 2023 October 26]. Available at http://www.statistics.gov.lk/Population/StaticalInformation/CPH2024
- 27. Central Bank of Sri Lanka. Overview of financial system stability | Central Bank of Sri Lanka. [Internet]. 2023. [cited 2023 October 26]. Available at https://www.cbsl.gov.lk/en/financial-system/financial-587 system-stability/overview
- 28.
Ministry of Education Sri Lanka (MOE) [Internet]. [cited 2024 Sep 12]. Available from: https://moe.gov.lk/
- 29. Arksey HO’Malley L. Scoping studies: towards a methodological framework, International Journal of Social Research Methodology, 2007 Feb;8(1):19–32.
- 30. Levac D, Colquhoun H, O’Brien KK. Scoping studies: advancing the methodology. Implement Sci. 2010 Sep 20;5:69. pmid:20854677
- 31. Peters MD, Godfrey CM, Khalil H, McInerney P, Parker D, Soares CB. Guidance for conducting systematic scoping reviews. Int J Evid Based Healthc. 2015;13(3):141–146. pmid:26134548
- 32.
Peters MDJ, Godfrey C, McInerney P, Munn Z, Tricco AC, Khalil H. Scoping Reviews (2020). Aromataris E, Lockwood C, Porritt K, Pilla B, Jordan Z, editors. JBI Manual for Evidence Synthesis. JBI; 2024. Available from: https://synthesismanual.jbi.global. https://doi.org/10.46658/JBIMES-24-09
- 33. Tricco AC, Lillie E, Zarin W, et al. PRISMA extension for scoping reviews (PRISMA-ScR): checklist and explanation. Ann Intern Med. 2018;169(7):467–473. pmid:30178033
- 34. Ouzzani M, Hammady H, Fedorowicz Z et al. Rayyan—a web and mobile app for systematic reviews. Syst Rev 5, 210 (2016). pmid:27919275
- 35. Pieris K, Uragoda CG. A Bibliography of medical publications relating to Sri Lanka, 1811–1976. Colombo: National Science Council of Sri Lanka, Social Science Research Centre; 1980.
- 36. Uragoda CG. Bibliography of medical publication relation of Sri Lanka 1981–1988.39. Pieris KS. A bibliography on health in Sri Lanka, 1977–1980. Available from: https://dl.nsf.gov.lk/handle/1/18203
- 37. Pieris KS. A bibliography on health in Sri Lanka, 1977–1980. Available from: https://dl.nsf.gov.lk/handle/1/18203
- 38. Page MJ, McKenzie E, Bossuyt PM, Boutron I, Hoffmann TC, Mulrow CD et al. The PRISMA 2020 statement: an updated guideline for reporting systematic reviews BMJ 2021; 372:n71 pmid:33782057
- 39. Munn Z, Tufanaru C, Aromataris E. JBI’s systematic reviews: data extraction and synthesis. Am J Nurs. 2014 Jul;114(7):49–54. pmid:25742352
- 40. Wells GA, Shea B, O’Connell Da, Peterson J, Welch V, Losos M, et al. The Newcastle-Ottawa Scale (NOS) for assessing the quality of nonrandomised studies in meta-analyses. Oxford; 2000.Available from: https://www.researchgate.net/publication/261773681
- 41. Levecke B, Easton AV, Cools P, Albonico M, Ame S, Gilleard JS, et al. The optimal timing of post-treatment sampling for the assessment of anthelminthic drug efficacy against Ascaris infections in humans. Int J Parasitol Drugs Drug Resist. 2018 Apr;8(1):67–69. Epub 2018 Jan 13. pmid:29414108
- 42. Goodwin LG, Jayewardene LG, Standen OD. Clinical trials with bephenium hydroxynaphthoate against hookworm in Ceylon. Br Med J. 1958 Dec 27;2(5112):1572–6. pmid:13608052
- 43. Jayewardene G, Ismail MM, Wijayaratnam Y. Bephenium hydroxynaphthoate in treatment of ascariasis. Br Med J. 1960 Jul 23;2(5194):268–71. pmid:14406934
- 44. Senewiratne B, Hettiarachchi J, Senewiratne K. A comparative study of the relative efficacy of pyrantel pamoate, bephenium hydroxynaphthoate and tetrachlorethylene in the treatment of Necator americanus infection in Ceylon. Ann Trop Med Parasitol. 1975 Jun;69(2):233–9. pmid:1155990
- 45. Lionel ND. Mebendazole in the treatment of intestinal helminthiasis with special reference to whipworm infection. J Trop Med Hyg. 1975 Apr;78(4):75–7. pmid:1171256.
- 46. Kumarendran B, Pathmeswaran A, De Silva NR. Effectiveness of mebendazole and health education in control of pinworm infection among children living in low-income settlements. Sri Lanka Medical Association, 130th Anniversary International Medical Congress. 2017;62 (Supplement 1):160
- 47. Ismail MM, Premaratne UN, Suraweera MG. Comparative efficacy of single dose anthelmintics in relation to the intensity of geohelminth infections. Ceylon Med J. 1991 Dec;36(4):162–7. pmid:1807845.
- 48. Sorensen E, Ismail M, Amarasinghe DK, Hettiarachchi I. The efficacy of three anthelmintic drugs given in a single dose. Ceylon Med J. 1996 Jun;41(2):42–5. pmid:8771941.
- 49. Balasuriya S, Edirisinghe JS, Rajudeen NM. Effectiveness of mass treatment with mebendazole in the control of soil transmitted helminths in Sri Lanka. Ceylon Med J. 1990 Mar;35(1):15–20. pmid:2361225.
- 50. Gunawardena NK, Kumarendran B, Manamperi NH, Senarathna BP, Silva M, Pathmeswaran A, et al. Randomized placebo-controlled trial of the efficacy of mebendazole polymorphs in the treatment of hookworm infections. Proceedings of the Annual Meeting of the American Society of Tropical Medicine and Hygiene. 2013; 62:313
- 51. De Silva DG, Lionel ND, Jayatilleka SM. Flubendazole in the treatment of Ascaris lumbricoides and Trichuris trichiura: a comparison of two different regimens with single-dose. Ceylon Med J. 1984 Dec;29(4):199–203. pmid:6543679.
- 52. De Silva HDG, Lionel ND, Premaratne UN, Warnasuriya N, Soysa PE. Flubendazole in the treatment of soil transmitted helminths. Ceylon Med J. 1987 Sep;32(3):129–32. pmid:3447751.
- 53. Fernando MA, Balasuriya S. Control of ascariasis by mass treatment with piperazine citrate. Ceylon Med J. 1977 Sep;22(3):120–8. pmid:616343
- 54. Ismail MM, Jayakody RL. Efficacy of albendazole and its combinations with ivermectin or diethylcarbamazine (DEC) in the treatment of Trichuris trichiura infections in Sri Lanka. Ann Trop Med Parasitol. 1999 Jul;93(5):501–4. pmid:10690245
- 55. De Silva DG, Lionel ND, Premaratne UN, Warnasuriya N, Soysa PE. Single dose treatment of mixed helminth infections—comparison of three different regimes. Ceylon Med J. 1987 Mar;32(1):49–52. pmid:3690729.
- 56. Gunawardena NK, Chandrasena TN, de Silva NR. Prevalence of enterobiasis among primary school children in Ragama, Sri Lanka. Ceylon Med J. 2013 Sep;58(3):106–10. pmid:24081170
- 57. Chellappah SF. Public health aspects of Ancylostomiasis. J Ceylon Branch Br Med Assoc Vol. 1938;35(1):419–45.
- 58. Rasaratnam K, Murugananthan A, Kannathasan S. Prevalence and associated factors of soil transmitted helminthes infestation among preschool children of Vadamaradchi Educational Zone. Ving. Journal of Science 2011,10(1):25–34.
- 59. Fernando SD, Paranavitane SR, Rajakaruna J, Weerasinghe S, Silva D, Wickremasinghe AR. The health and nutritional status of school children in two rural communities in Sri Lanka. Trop Med Int Health. 2000 Jun;5(6):450–2. pmid:10929146
- 60. Fernando SD, Goonethilleke H, Weerasena KH, Kuruppuarachchi ND, Tilakaratne D, de Silva D, Wickremasinghe AR. Geo-helminth infections in a rural area of Sri Lanka. Southeast Asian J Trop Med Public Health. 2001 Mar;32(1):23–6. pmid:11485089.
- 61. Selvaratnam RR, de Silva LD, Pathmeswaran A, de Silva NR. Nutritional status and productivity of Sri Lankan tea pluckers. Ceylon Med J. 2003 Dec; 48(4):114–8. pmid:15125401
- 62. De Silva NR, Pathmeswaran A, Fernando SD, Weerasinghe CR, Selvaratnam RR, Padmasiri EA, Montresor A. Impact of mass chemotherapy for the control of filariasis on geohelminth infections in Sri Lanka. Ann Trop Med Parasitol. 2003 Jun;97(4):421–5. pmid:12831528
- 63. Chandrasena TG, de Alwis AC, de Silva LD, Morel RP, de Silva NR. Intestinal parasitoses and the nutritional status of Veddah children in Sri Lanka. Southeast Asian J Trop Med Public Health. 2004 Jun;35(2):255–9. pmid:15691120.
- 64.
Gunawardena GSA, Karunaweera ND, Ismail MM. A study on the seasonal variation in the incidence of Ascaris infection in the plantation sector of Sri Lanka. In: Collected papers on the control of soil-transmitted helminthiases. Asian Parasite Control Organization, Eds. Hayashi S et al., 2001,VII: 104–112.
- 65. Pathmeswaran A, Jayatissa R, Samarasinghe S, Fernando A, de Silva RP, Thattil RO, de Silva NR. Health status of primary schoolchildren in Sri Lanka. Ceylon Med J. 2005 Jun;50(2):46–50. pmid:16114767
- 66. Banneheke BMHA, Gunawardane DMDE, Pinidiyapathirage M, Ekanayake S, Withana R, Tilakaratne WD. Geohelminthic infection in an estate child population in Sri Lanka: association with hygienic practices and eosinophil counts. Bull Sri Lanka Coll Microbiol. 2006;04(1):16. Available from: tp://repository.kln.ac.lk/handle/123456789/13305
- 67. Chandrasena TG, Hapuarachchi HC, Dayanath MY, Pathmeswaran A, de Silva NR. Intestinal parasites and the growth status of internally displaced children in Sri Lanka. Trop Doct. 2007 Jul;37(3):163–5. pmid:17716506
- 68. Gunawardena NK, Amarasekera ND, Pathmeswaran A, de Silva NR. Effect of repeated mass chemotherapy for filariasis control on soil-transmitted helminth infections in Sri Lanka. Ceylon Med J. 2008 Mar;53(1):13–6. pmid:18590264
- 69. Chandrasena TG, Balasooriya BA, Imbulpitiya IV, de Silva NR. A survey for intestinal parasites in a psychiatric institution in Sri Lanka. Ann Trop Med Parasitol. 2010 Oct;104(7):605–8. pmid:21092398
- 70.
Kumarendran B. Soil-transmitted helminth infections among plantation sector primary school children in Nuwara Eliya District. Available from: http://192.248.21.144/handle/1/1343
- 71. Gunawardena NK, Gunasingha HMMSK, Kumarendran B, Pathmeswaran A, de Silva NR. Prevalence of soil-transmitted helminth infections and malnutrition among 9–10 year old children attending estate sector schools. The Ceylon Medical Journal. 2010; 55(Supplement 1):28. Available from: http://repository.kln.ac.lk/handle/123456789/9889
- 72. Gunawardena K, Kumarendran B, Ebenezer R, Gunasingha MS, Pathmeswaran A, de Silva N. Soil-transmitted helminth infections among plantation sector schoolchildren in Sri Lanka: prevalence after ten years of preventive chemotherapy. PLoS Negl Trop Dis. 2011 Sep;5(9):e1341. pmid:21980549
- 73. Rathnayaka RMK, Wang . Prevalence and effect of personal hygiene on the transmission of helminth infection among primary school children living in slums. Int J Multidiscip Res Rev. 2012 Jul 1;2:1–13. Available from: https://www.researchgate.net/publication/317064458_prevalence_and_effect_of_personal_hygiene_ontransmission_of_helminthes_infection_among_primary_school_children_living_in_slums
- 74. Gunawardena S, Gunatilleke H, Ismail M. Prevalence of Enterobius vermicularis infection among schoolchildren attending four selected schools in the Hambantota district of Sri Lanka. Sri Lankan J Infect Dis. 2013; 3(2):17–20.
- 75. Gunawardena S, Gunawardena NK, Kahathuduwa G, Karunaweera ND, de Silva NR, Ranasinghe UB, Samarasekara SD, Nagodavithana KC, Rao RU, Rebollo MP, Weil GJ. Integrated school-based surveillance for soil-transmitted helminth infections and lymphatic filariasis in Gampaha district, Sri Lanka. Am J Trop Med Hyg. 2014 Apr;90(4):661–6. pmid:24493672
- 76. Suraweera O, Galgamuwa L, Iddawela D, Wickramasinghe S. Prevalence and associated factors of Enterobius vermicularis infection in children from a poor urban community in Sri Lanka: a cross-sectional study. Int J Res Med Sci. 2015; 3(8):1994–1999.
- 77. Galgamuwa L, Iddawela D, Dharmaratne SD. Factors associated with the prevalence of Ascaris lumbricoides infection among preschool children in a plantation community, Kandy district, Sri Lanka. Southeast Asian J Trop Med Public Health. 2016 Nov;47(6):1143–52. pmid:29634161.
- 78. Kumarendran B, Pathmeswaran A, NR D. Prevalence of pinworm infection among children living in low income settlements in Colombo municipal council area. Sri Lanka Medical Association, 130th Anniversary International Medical Congress.2017;62(Supplement 1):94
- 79. Galgamuwa LS, Iddawela D, Dharmaratne SD. Prevalence and intensity of Ascaris lumbricoides infections in relation to undernutrition among children in a tea plantation community, Sri Lanka: a cross-sectional study. BMC Pediatr. 2018 Jan 25;18(1):13. pmid:29370780
- 80. Lepper HC, Prada JM, Davis EL, Gunawardena SA, Hollingsworth TD. Complex interactions in soil-transmitted helminth co-infections from a cross-sectional study in Sri Lanka. Trans R Soc Trop Med Hyg. 2018 Aug 1;112(8):397–404. pmid:30053259
- 81. Ubhayawardana N, Gammana Liyanage I, Herath HMJCB, Amarasekera U, Dissanayake T, de Silva S, Fernando N, Ekanayake S. Direct microscopy of stool samples for determining the prevalence of soil-transmitted helminthic infections among primary school children in Kaduwela MOH area of Sri Lanka following floods in 2016. J Environ Public Health. 2018 Jun 10;2018:4929805. pmid:29983716
- 82. Galgamuwa LS, Iddawela D, Dharmaratne SD. Association between intestinal helminth infections and mid-upper-arm circumference among children in Sri Lanka: a cross-sectional study. J Helminthol. 2018 May; 92(3):291–297. pmid:28615087
- 83. Suraweera O, Galgamuwa L, Wickramasinghe S, Iddawela D, Nandasiri N. Soil-transmitted helminth infections, associated factors and nutritional status in an estate community in Sri Lanka. Sri Lankan J Infect Dis. 2018;8(2):100.
- 84. Chandrasena TGAN, Hapuarachchi HAC, Dayanath MYD, de Silva NR. Intestinal parasitoses and the nutritional status of internally displaced children in Vavuniya. The Ceylon Medical Journal. 2005; 50(Supplement 1):40. Available at: http://repository.kln.ac.lk/handle/123456789/9941
- 85. Gunawardena GS, Karunaweera ND, Ismail MM. Socio-economic and behavioural factors affecting the prevalence of Ascaris infection in a low-country tea plantation in Sri Lanka. Ann Trop Med Parasitol. 2004 Sep;98(6):615–21. pmid:15324467
- 86. Edirisinghe JS, Weilgama DJ. Soil contamination with geohelminth ova in a tea plantation. Ceylon Med J. 1997 Dec;42(4):167–72. pmid:9476399.
- 87. Sorensen E, Ismail M, Amarasinghe DK, Hettiarachchi I, Dassenaieke TS. The effect of the availability of latrines on soil-transmitted nematode infections in the plantation sector in Sri Lanka. Am J Trop Med Hyg. 1994 Jul;51(1):36–9. pmid:8059913
- 88. Perera PJ, Disanayake D, Fernando MP, Warnakulasoority TD, Ranathunga N. Knowledge and practices related to helminth infections among mothers living in a suburban area of Sri Lanka. Southeast Asian J Trop Med Public Health. 2012 Nov;43(6):1326–32. pmid:23413694.
- 89. Sri Lanka budget brief. (2021) Water sanitation and hygiene (wash) sector Sri Lanka 2021. Available from: https://www.unicef.org/srilanka/reports/budget-brief-water-sanitation-and-hygiene-wash-sector
- 90. Becker SL, Liwanag HJ, Snyder JS, Akogun O, Belizario V Jr, Freeman MC, et al. Toward the 2020 goal of soil-transmitted helminthiasis control and elimination. PLoS Negl Trop Dis. 2018 Aug 14;12(8):e0006606. pmid:30106975
- 91. The World Bank. (2021) Sri Lanka needs new water and sanitation policies to unlock investment barriers. Available from: https://www.worldbank.org/en/news/feature/2021/08/31/sri-lanka-needs-new-water-and-sanitation- policies-to-unlock-investment-barriers. 2021;2021.
- 92.
The Adventist Development and Relief Agency (ADRA) Sri Lanka.Water, sanitation and hygiene (WASH), Available from: https://adrasrilanka.org/impact/wash
- 93. Ministry of Health (MOH). Guidelines on de-worming children and pregnant women against soil-transmitted helminths in the community setting, 2019–2022, No:01-58/2018, Sri Lanka General circular. 2018.
- 94. Dhakal S, Karim MJ, Al Kawsar A, Irish J, Rahman M, Tupps C, Kabir A, Imtiaz R. Post-intervention epidemiology of STH in Bangladesh: Data to sustain the gains. PLoS Negl Trop Dis. 2020 Dec 7;14(12):e0008597. pmid:33284834
- 95. Zhu H, Huang J, Zhou C, Zhu T, Qian M, Zhang M, Chen Y, Li S. Soil-transmitted helminthiasis—China, 2018. China CDC Wkly. 2020 Jan 17;2(3):34–38. pmid:34594705.
- 96. Phillips AE, Ower AK, Mekete K, Liyew EF, Maddren R, Mengistu B, et al. Baseline soil-transmitted helminth and schistosome infection in the Geshiyaro project, Ethiopia: A unique transmission interruption project using biometric fingerprinting for longitudinal individual analysis. PLoS Negl Trop Dis. 2023 Oct 18;17(10):e0011589. pmid:37851666
- 97. Idowu OA, Babalola AS, Olapegba T. Prevalence of soil-transmitted helminth infection among children under 2 years from urban and rural settings in Ogun state, Nigeria: implication for control strategy. Egypt Pediatr Assoc Gaz. 2022;70(1):5.
- 98. Aung E, Han KT, Gordon CA, Hlaing NN, Aye MM, Htun MW, et al. High prevalence of soil-transmitted helminth infections in Myanmar schoolchildren. Infect Dis Poverty. 2022 Mar 10;11(1):28. pmid:35272701
- 99. Chong NS, Smith SR, Werkman M, Anderson RM. Modelling the ability of mass drug administration to interrupt soil-transmitted helminth transmission: Community-based deworming in Kenya as a case study. PLoS Negl Trop Dis. 2021 Aug 2;15(8):e0009625. pmid:34339450
- 100. Pan American Health Organization (PAHO). Regional Meeting to boost efforts for the control of soil-transmitted helminth infections (geohelminthiasis) in the Americas. (Lima, 1–3 August 2016). Pan American Health Organization.Available from: https://www.paho.org/en/documents/regional-meeting-boost-efforts-control-soil-transmitted-helminth-infections.
- 101. Casulli A. New global targets for NTDs in the WHO roadmap 2021–2030. PLoS Negl Trop Dis. 2021;15(5):e0009373. Published 2021 May 13. pmid:33983940
- 102. Ngwese MM, Manouana GP, Moure PAN, Ramharter M, Esen M, Adégnika AA. Diagnostic techniques of soil-transmitted helminths: impact on control measures. Trop Med Infect Dis. 2020 Jun 5;5(2):93. pmid:32516900
- 103. O’Connell EM, Nutman TB. Molecular Diagnostics for soil-transmitted helminths. Am J Trop Med Hyg. 2016 Sep 7; 95(3):508–513. pmid:27481053