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      Toward the 2020 goal of soil-transmitted helminthiasis control and elimination

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          Introduction On May 22, 2001, a resolution passed during the 54th World Health Assembly (WHA 54.19) took an historic step toward reducing the morbidity and mortality associated with the world’s most common parasitic worm (helminth) infections [1]. Indeed, an estimated 1.45 billion individuals are infected with soil-transmitted helminths worldwide [2]. The soil-transmitted helminths primarily comprise hookworm (Ancylostoma duodenale and Necator americanus), roundworm (Ascaris lumbricoides), and whipworm (Trichuris trichiura). Taken together, soil-transmitted helminthiasis accounts for a global burden of over 3.3 million disability-adjusted life years [3] and is associated with anemia [4], malnutrition [5], and impaired physical and cognitive development [6–9]. As the primary recommendation to eliminate soil-transmitted helminthiasis as a public health problem, WHA 54.19 called for improved water and sanitation to reduce transmission and urged that 3 high-risk groups receive regular treatment with anthelmintic drugs: preschool-aged children (PSAC), school-aged children (SAC), and women of reproductive age (WRA) [1]. During the decade 2001–2010, however, soil-transmitted helminthiasis control focused almost exclusively on preventive chemotherapy targeting SAC through the education sector, with a target of achieving at least 75% drug coverage in this population group by 2010 (Table 1). While this target was not reached [10], global efforts to address soil-transmitted helminthiasis were renewed in 2011, when several high-level meetings took place and their reports published in subsequent years. The “Roadmap on Neglected Tropical Diseases” was published first, reiterating the 75% preventive chemotherapy coverage target for PSAC and SAC [11]. This roadmap inspired 22 partners from public and private sectors to endorse the London Declaration on Neglected Tropical Diseases [12] and called on all partners to sustain and expand programs to achieve the 2020 goals outlined in the roadmap. Subsequently, a specific strategic plan for soil-transmitted helminthiasis was published, also in 2012, in which, on top of the 75% target for coverage, the additional target of reducing moderate- and heavy-intensity infections (defined as the number of helminth eggs excreted by an individual exceeding a preset, species-specific threshold, used as a proxy for worm burden) to less than 1% among SAC was affirmed [13]. With 2020 on the horizon, we are well into the second decade post-WHA 54.19. Major challenges remain. Among others, these include (1) the need to maximize the impact of pharmaceutic donations of anthelmintic drugs, (2) the need to clarify targets to guide monitoring efforts moving forward, and (3) the need to take into account recent successes of the Global Program to Eliminate Lymphatic Filariasis (GPELF). The latter challenge results in the consequent scaling down of community-based control interventions, thus reducing the ancillary benefits of this strategy on soil-transmitted helminthiasis [14]. A complete transition from a lymphatic filariasis elimination program to a soil-transmitted helminthiasis control program will have important consequences so that efforts to ensure that all risk groups for soil-transmitted helminthiasis will be adequately covered need to be planned well in advance of the actual transition. 10.1371/journal.pntd.0006606.t001 Table 1 Overview of the evolution of documents published by WHO pertaining to the control of soil-transmitted helminthiasis since 2001. Year Document Goal Risk group(s) Controlling morbidity: specific targets Parasitologic monitoring:specific targets 2001 WHA 54.19 [1] “To sustain successful control activities in low-transmission areas in order to eliminate soil transmitted helminth infections as a public health problem, and to give high priority to implementing or intensifying control of soil transmitted helminth infections in areas of high transmission” (p. 1) PSAC, SAC, WRA • “Regular administration of chemotherapy to at least 75%, and up to 100%, of all school-age children at risk of morbidity by 2010” (p. 1) Not mentioned 2002(Second edition published in 2012) Helminth Control in School-age Children [77] “Reduce worm loads [in SAC] and keep them low” (p. 8) SAC • “Regular delivery of anthelminthic treatment to at least 75% of school-age children in endemic areas” (p. 8) • “The proportion of children heavily infected has been reduced to less than 1% in 2–3 years” (p. 44)• “The proportion of children with morbidity resulting from STH [soil transmitted helminth] infection and/or schistosomiasis has been reduced to less than 1% in 5 years” (p. 44) 2012 WHO Strategic Plan 2011–2020 [13] “Reduce morbidity from STH [soil-transmitted helminthiasis] in preschool-aged children (aged 1–4 years) and school-age children (aged 5–14 years) to a level below which it would not be considered a public health problem1” (p. 20) PSAC, SAC • “75–100% of children (SAC and PSAC) needing preventive chemotherapy worldwide have been treated [by 2020]” (pg. 29)• “100% of countries requiring preventive chemotherapy for STH [soil transmitted helminthiasis] have achieved 75% national coverage of SAC and PSAC [by 2020]” (p. 29) • “Less than 1% of countries requiring preventive chemotherapy for STH [soil-transmitted helminthiasis] have infection of high or moderate intensity [by 2020]” (p. 29)• “100% of countries requiring preventive chemotherapy for STH [soil-transmitted helminthiasis] regularly assess intensity of infections in sentinel sites [by 2020]” (p. 29) 2012 WHO 2020 Roadmap on Neglected Tropical Diseases [11] Soil-transmitted helminthiasis is included under diseases listed with “targets and milestones for control of neglected tropical diseases, 2015–2020” (p. 19) PSAC, SAC • “75% of preschool and school-aged children in need of treatment are regularly treated [by 2020]” (p. 5)• “75% coverage achieved in preschool and school-aged children in 100% of countries [by 2020]” (p. 19) Not mentioned Abbreviations: PSAC, preschool-aged children; SAC, school-aged children; WHA, World Health Assembly; WHO, World Health Organization; WRA, women of reproductive age. 1 Soil-transmitted helminthiasis is considered a public health problem when the prevalence of soil-transmitted helminth infection of moderate and heavy intensity among SAC is over 1%. If the goal of eliminating soil-transmitted helminthiasis as a public health problem is to be achieved, it is important to proactively review and address gaps in disease control programs. The Soil-Transmitted Helminthiasis Advisory Committee (subsequently termed “the Committee,” established in 2012, as the successor of the Mebendazole Advisory Committee that was launched in 2006) is an independent group of experts that holds an annual meeting to assess challenges and review progress made in soil-transmitted helminthiasis control, including operational research, monitoring, and evaluation, and to deliberate on next steps. The Committee makes recommendations to address technical and scientific challenges and provides advice to members of the Soil-Transmitted Helminthiasis Coalition and the World Health Organization (WHO) Strategic and Technical Advisory Group (STAG). On October 18–19, 2016, the Committee convened for 2 days in Basel, Switzerland, to review and discuss advances in operational research, anthelmintic treatment options, and diagnostic tools and strategies. Furthermore, programmatic and strategic challenges in global control efforts were debated. Here, we present the recommendations arising from this meeting and highlight challenges and potential solutions on the road toward the 2020 goal of soil-transmitted helminthiasis control and elimination and beyond. Controlling soil-transmitted helminthiasis morbidity Progress and challenges The Soil-Transmitted Helminthiasis Strategic Plan 2011–2020 [13] has outlined 4 primary milestones for global control of soil-transmitted helminthiasis: (1) 100% of countries requiring preventive chemotherapy for soil-transmitted helminthiasis have achieved 75% national coverage of PSAC and SAC, (2) these countries regularly assess intensity of soil-transmitted helminth infections in sentinel sites, (3) less than 1% of countries requiring preventive chemotherapy for soil-transmitted helminthiasis have infection of moderate or high or intensity by 2020, and (4) 75%–100% of PSAC and SAC needing preventive chemotherapy worldwide have been treated. In 2016, the Weekly Epidemiological Record (WER) reported the global progress toward milestones 1 and 4, indicating that <30% of countries requiring preventive chemotherapy for soil-transmitted helminthiasis had achieved the 75% national coverage target for PSAC and SAC and that 48% of PSAC and 65% of SAC needing preventive chemotherapy worldwide had received treatment [15]. It was not possible to report on either milestone 2 or 3 because there were no publicly available data to review whether sentinel surveillance or parasitologic monitoring was being implemented in the endemic countries. Based on current progress toward milestones 1 and 4, it is anticipated that these may potentially be achieved by 2020 (at least for SAC), whereas milestones 2 and 3 are less likely to be reached by 2020. Using the London Declaration Scorecard (http://unitingtocombatntds.org/reports/5th-report/), the Committee noted that milestones for country reporting on coverage and parasitologic monitoring were lagging. In order to bring progress toward milestones 2 and 3 on track, the Committee suggests that barriers to program implementation be acknowledged and that technical support be provided to countries struggling to reach the 75% national coverage targets. As the year 2020 nears, there is a pressing need for the global community to consider a serious recommitment to milestones 2 and 3 and to work together to improve parasitologic assessment in affected countries. The London Declaration Scorecard remains a useful tool in monitoring progress toward these milestones, but the Committee recommends that the Scorecard be updated to include water, sanitation, and hygiene (WASH) indicators to be aligned with the United Nations Sustainable Development Goals (SDGs; http://www.un.org/sustainabledevelopment/sustainable-development-goals/) and that treatment be expanded to include other at-risk groups, most importantly WRA. Beyond being explicitly called for in WHA 54.19, these additional measures will likely be needed to accelerate elimination of soil-transmitted helminthiasis as a public health problem in children [16–20]. In this context, a robust, integrated, and regularly updated global surveillance platform is needed. Ideally, this platform could also be used for schistosomiasis and other neglected tropical diseases [21,22]. The Committee also recognizes the unique contribution of GPELF to concurrently control soil-transmitted helminthiasis–related morbidity. Launched in 2002 by WHO, GPELF has successfully treated an estimated 36 million PSAC and 139 million SAC in 2015 with combination preventive chemotherapy that included albendazole [23], one of the two donated anthelmintic drugs widely used against soil-transmitted helminthiasis [24]. The GPELF community-based delivery platform reaches at-risk groups outside of the school setting and through the coadministration of 2 drugs with a different mechanism of action (e.g., albendazole and ivermectin) that, as shown for animal helminthiasis, are likely to reduce the risk of resistance [25,26]. It follows that GPELF has enhanced the coverage and effectiveness of soil-transmitted helminthiasis control activities in many countries. However, there is an immediate risk of losing this delivery infrastructure as the GPELF achieves its goal and as national governments and donors scale down or discontinue their support for the program. Hence, without a strategic transition plan in place, communities that used to benefit from lymphatic filariasis control activities run the risk of undermining the gains already made for soil-transmitted helminthiasis control once GPELF is discontinued. The Committee therefore proposes that (1) a parasitologic assessment be first conducted in areas where termination of lymphatic filariasis control activities is being contemplated and that (2) WHO convenes a technical working group to develop a decision algorithm for countries on when and how to implement a lymphatic filariasis–soil-transmitted helminthiasis transition. Such an algorithm will be especially important in areas where there are no clear alternatives for continuing preventive chemotherapy for soil-transmitted helminthiasis among SAC and other at-risk groups [27,28]. Clearly, eliminating soil-transmitted helminthiasis as a public health problem has to go beyond preventive chemotherapy for SAC alone, as other groups at risk also serve as a reservoir of infection, e.g., hookworm infections frequently predominate in adult populations [29]. Coverage of preventive chemotherapy for PSAC continues to lag behind the coverage for SAC; to date, there is no regular preventive chemotherapy program against soil-transmitted helminthiasis for WRA (although, some countries have developed such programs specifically for pregnant women). To address these gaps, we recommend that specific guidelines for the treatment of PSAC and WRA be developed and validated under the lead of WHO, including a regular reporting mechanism for the treatment coverage in these groups. Taken together, there is a need for a robust, integrated, and regularly updated global neglected tropical disease surveillance platform to include interactive preventive chemotherapy data (http://apps.who.int/gho/cabinet/pc.jsp) and georeferenced survey and intervention data (https://www.gntd.org) [22,30]. Treatment options and new developments In comparison to other classes of anti-infective drugs such as antibiotics, the number of anthelmintics that are used in human medicine is limited, and there have been far fewer innovations or new compounds developed to broaden the pharmacologic armamentarium [24,31–34]. In this context, several important challenges for soil-transmitted helminthiasis control need to be highlighted, i.e., (1) the development of a new and rapidly disintegrating, chewable formulation of mebendazole for PSAC; (2) the introduction of combination treatment approaches for soil-transmitted helminthiasis; (3) the limited understanding of resistance development to anthelmintic drugs in human soil-transmitted helminthiasis; and (4) careful considerations pertaining to the continuing role of pharmaceutic drug donations in the post-2020 agenda. Albendazole and mebendazole, both benzimidazole drugs, are widely used in preventive chemotherapy programs targeting soil-transmitted helminthiasis worldwide. Their anthelmintic properties differ slightly, with albendazole being more active against hookworm [31,35]. Of note, the efficacy of both compounds against T. trichiura is unsatisfactory, and low cure rates of single-dose administration have also been reported for hookworm infection, in particular if mebendazole is used. Other factors, such as suboptimal dissolution of the tablets, may further decrease their therapeutic effects [36]. In addition, PSAC, especially those less than 3 years of age, have difficulty chewing and swallowing the relatively large tablets [37], and several deaths have been caused by aspiration and choking [38]. Hence, the Committee welcomes the recent approval of a new, rapidly disintegrating chewable formulation of mebendazole. The drug’s efficacy and tolerability have been shown in a study conducted in Ethiopia and Rwanda [37], and the drug received approval by the United States Food and Drug Administration (FDA) on October 19, 2016. We now advocate that access to this new formulation be provided in endemic areas, particularly for preventive chemotherapy targeting PSAC. It has been suggested that widespread use of monotherapy might facilitate the development of anthelmintic drug resistance [39–44]. Hence, as for other chronic infections (e.g., tuberculosis, human immune deficiency virus [HIV], and malaria), combination therapy against soil-transmitted helminthiasis might decrease this risk and could enhance efficacy [25]. Moreover, the need for combination therapy is further supported by coendemicity of multiple helminth infections. Indeed, in many endemic settings, infections due to A. lumbricoides, hookworm, and T. trichiura co-occur. Recent studies reported an improved drug efficacy if a combination of albendazole plus either ivermectin or oxantel pamoate was administered [45–47]. An overview of currently used anthelmintics and promising drug combinations is presented in Table 2. Logistically, it would be desirable to develop coformulations of drug combinations that could be distributed as a single tablet (such combinations are readily available for other conditions, e.g., arterial hypertension, HIV/AIDS, and tuberculosis), but pharmacologic challenges need to be resolved before this approach becomes feasible in daily practice. While combination therapy may temporarily lower the resistance pressure, there is also a clear need for new anthelmintic drugs to ensure access to efficacious treatment options in the future. Additionally, ongoing research on developing anthelmintic vaccines can also provide important additional control tools, which may be integrated into future control strategies. The Committee urges that further studies be conducted to identify the most promising drug combinations for preventive chemotherapy against soil-transmitted helminthiasis. It applauds new funding granted by the Bill & Melinda Gates Foundation that addresses some of these issues, which has already resulted in the addition of the albendazole plus ivermectin combination to the WHO Model List of Essential Medicines [48]. Additionally, we welcome ongoing research projects that will strengthen the monitoring and surveillance of drug efficacy and anthelmintic resistance in soil-transmitted helminthiasis control programs (e.g., the Bill & Melinda Gates Foundation-funded STARWORMS [Stop Anthelminthic Resistant WORMS] project; http://www.starworms.org). 10.1371/journal.pntd.0006606.t002 Table 2 Efficacy of anthelmintic drugs used for the treatment of soil-transmitted helminthiasis and recent evidence from clinical trials pertaining to 3 drug combinations. Single drug Spectrum of activity against soil-transmitted helminthiasis Reference Ascaris lumbricoides Hookworm Trichuris trichiura Albendazole +++ ++ + [24] Levamisole +++ + + [34] Mebendazole +++ + + [78] Pyrantel pamoate +++ + + [34] Drug combinations Available evidence from clinical trials Reference(s) Albendazole + ivermectin • Improved activity against T. trichiura • Potentially less reinfection than after monotherapy with albendazole alone• Ivermectin is active against Strongyloides stercoralis [46,47,79] Albendazole + oxantel pamoate • Highest activity of tested drug combinations against T. trichiura • Less reinfection than after monotherapy with albendazole alone [45, 47] Tribendimidine + oxantel pamoate or ivermectin • Noninferior efficacy profile to albendazole + oxantel pamoate• Ivermectin is active against S. stercoralis [80] Abbreviations: +++, excellent efficacy (cure rates >90%); ++, moderate efficacy (50%–90%); +, low efficacy (<50%). Experience and lessons from preventive chemotherapy programs targeting millions of mainly SAC were only possible through drug donations by the manufacturing pharmaceutic industry. However, it is important to note that a long-lasting, durable strategy for soil-transmitted helminthiasis control or even elimination cannot solely rely on such drug donation programs. As generic deworming drugs will become increasingly important in the future, particularly in the post-2020 agenda, the Committee urges WHO to encourage prequalification of the manufacturers of these drugs. Parasitologic monitoring Progress and challenges Survey methods currently endorsed by WHO to assess the prevalence of any soil-transmitted helminth infection are not designed to determine whether or not the goal of eliminating soil-transmitted helminthiasis as a public health problem in children has been achieved. Hence, there is a need to develop a new survey design that (1) is sufficiently powered to assess if the prevalence of moderate- or heavy-intensity infections falls below 1% and (2) is feasible and affordable, considering the limited resources and capacity of national soil-transmitted helminthiasis control programs. Any new methodology being proposed should enable the measurement of prevalence of soil-transmitted helminth infection in SAC, PSAC, WRA, and other risk groups, providing a more complete picture of the burden of soil-transmitted helminthiasis in the entire community [49]. The Committee urges WHO to spearhead discussions with stakeholders to refine this survey methodology and, after successful field validation, to support and endorse its use so that it can be adopted by countries before 2020. At the same time, areas where the prevalence of soil-transmitted helminth infection continues to be high despite several years of preventive chemotherapy would warrant further investigation as these serve as potential indicators of previously unrecognized programmatic challenges. Diagnostic methods and new developments Accurate diagnostic techniques for soil-transmitted helminth infection are of paramount importance in settings where the overall prevalence is low and, even more importantly, where the majority of infections are of light intensity. Indeed, different diagnostic techniques are required at different stages of helminthiasis control programs, e.g., to prove elimination as a public health problem or to document an interruption of transmission. The detection limit of most diagnostic techniques decreases considerably in such areas, and techniques with a higher sensitivity are required for an accurate assessment of remaining foci of endemicity [50]. It has recently been argued that the development of new and more sensitive diagnostic techniques has been slowed down by the strong focus on drug coverage rather than parasitologic monitoring in most soil-transmitted helminthiasis control programs [51]. The development of several new techniques, many of which are not based on stool microscopy, are encouraging. Their different features and characteristics are summarized in Table 3. 10.1371/journal.pntd.0006606.t003 Table 3 Brief characterization of the Kato–Katz technique and selected other diagnostic developments for detection of soil-transmitted helminths, which might potentially be used in soil-transmitted helminthiasis control programs and epidemiologic surveys. Diagnostic technique Principle Characteristics Reference(s) Kato-Katz thick-smear • Smear-based stool microscopy• Detection is based on the morphology of eggs • WHO-recommended standard technique for epidemiologic surveys• Examination of 41.7 mg of stoolSimultaneous detection of soil-transmitted helminth and Schistosoma eggs• Relatively simple to perform• Sensitivity dependent on infection intensity (unreliable in populations with a low prevalence and light infection intensity) and number of thick smears prepared• Hookworm eggs are not reliably detected after 30–60 min [81–83] Mini-FLOTAC • Flotation-based stool microscopy• Detection is based on the morphology of eggs, larvae, and cysts • Further development of the original FLOTAC technique, without need for centrifugation (hence, no electricity required)• One of the WHO-recommended methods in transmission assessment surveys• Examination of 100 mg of stool• Simultaneous detection of helminth eggs (soil-transmitted helminths and Schistosoma spp.), larvae, and intestinal protozoa (Giardia intestinalis, Entamoeba spp.) depends on the choice of flotation solution [84–86] FECPAKG2 • Flotation-based stool microscopy• Detection is based on the morphology of the eggs • Initially developed for the diagnosis of animal soil-transmitted helminths but currently being optimized and validated for human soil-transmitted helminths• Currently only available for the diagnosis of veterinary soil-transmitted helminths• Examination of approximately 3 g of stool• Allows accumulation of eggs in 1 microscopic view, digital images are taken by an autonomously operating digital picture microscope, images are sent via e-mail for analysis elsewhere• Waives the need for laboratory infrastructure in epidemiologic studies• Holds promise for quality assurance activities [87–89] PCR • Nucleic acid-based molecular technique• Detection of specific nucleic acid sequences of target pathogens • Allows differentiation of zoonotic and human soil-transmitted helminth species• Technically difficult, requires well-equipped laboratories with constant power supply and experienced laboratory technicians• No well-established quality assurance system for PCR diagnostics for soil-transmitted helminth infection is currently in place• Concurrent detection of several helminth and intestinal protozoa species possible [90] RPA • Nucleic acid-based molecular technique• Detection of specific nucleic acid sequences of target pathogens • Highly sensitive and specific detection of pathogen-specific nucleic acids• No need for a thermal cycler; hence, no need for electricity• Available for intestinal protozoa, schistosomiasis and fascioliasis, but not (yet) for soil-transmitted helminthiasis [91,92] LAMP • Nucleic acid-based molecular technique• Detection of specific nucleic acid sequences of target pathogens • Characteristics similar to RPA• Several published studies reporting high sensitivity and specificity for detection of soil-transmitted helminth species [93,94] Abbreviations: LAMP, loop-mediated isothermal amplification procedure; PCR, polymerase chain reaction; RPA, recombinase polymerase amplification. As soil-transmitted helminthiasis control efforts evolve, diagnostic techniques must also be further developed to ensure that their application is feasible and that the reported results are accurate. In areas where preventive chemotherapy has been employed for many years, conventional techniques based on stool microscopy alone might fail to demonstrate the persistence of light-intensity infections [50,52]. In such instances, more sensitive molecular methods such as stool-based polymerase chain reaction (PCR) assays may depict the “true” situation more accurately. In settings of a very low prevalence of soil-transmitted helminth infection, pooling of stool specimens and subsequent PCR examination might be a promising method to detect and monitor areas of ongoing transmission, although costs and required logistic infrastructure require elaboration [53,54]. Additionally, a transition away from stool specimen analysis to, for example, blood- or urine-based tests for antigen or antibody detection might further enhance the accurate diagnosis of soil-transmitted helminthiasis [55,56]. For the aforementioned methods, in particular the molecular techniques, adequate specimen preservation, simplified nucleic acid extraction, and quality assurance systems are crucial [57]. This is important as many laboratories use a wide variety of in-house PCR techniques for detection of helminths, but target genes and techniques used differ considerably. Following 2 expert meetings held in Ghent, Belgium and Annecy, France in mid-2016, recommendations were made to develop target product profiles for different use-cases and to prepare field sites for large-scale validation studies of helminth PCR techniques. The Committee encourages rigorous, multicenter evaluations and strategic developments for large-scale application and setups for external quality assurance systems of such PCR techniques in the field. Evolution of soil-transmitted helminthiasis control: Clarifying the goals When reviewing the different documents pertaining to the global strategy against soil-transmitted helminthiasis (Table 1), the roadmap in particular fails to mention previous targets with respect to coverage and morbidity reduction. The Committee therefore urges WHO to ensure that all relevant future documentation reaffirm both morbidity control and parasitologic monitoring targets in order to allay any confusion or programmatic concerns. While the 2020 target of 75% drug coverage may be in reach for SAC—and perhaps PSAC [15]—in certain countries, it is likely that elimination of soil-transmitted helminthiasis as a public health problem will remain a challenge. In our view, rigorous parasitologic monitoring is required. The current strategy and the strong emphasis on drug coverage targets offer only indirect endpoints for national soil-transmitted helminthiasis control programs. A comparative assessment of the different strategies for soil-transmitted helminthiasis control and its arising implications for national control programs is presented in Table 4. The Committee supports a recent call [58] and stresses the importance for clarifying the goals of soil-transmitted helminthiasis control strategies. 10.1371/journal.pntd.0006606.t004 Table 4 Key characteristics of 3 different strategies pertaining to future soil-transmitted helminthiasis control efforts. Goal Priority Indicator Implications Original (and current) strategy: Deworm high-risk groups At least 75% of children in need of treatment are regularly treated • Endpoint: measurable endpoint but no indicator of morbidity, no stopping strategy• Parasitologic monitoring: limited monitoring required• Platform: school or child health day platforms may be adequate • Water, sanitation, and hygiene: integration advocated• Cost: least expensive• Research: little operational research required Revised strategy: Elimination of soil-transmitted helminthiasis as a public health problem Less than 1% moderate or heavy infection intensity prevalence in all risk groups • Endpoint: measurable endpoint, indirect indicator of morbidity• Parasitologic monitoring: intense monitoring required• Platform: integrated or community-based platform may be required• Water, sanitation, and hygiene: intense integration required• Cost: more expensive• Research: operational research required Ambitious strategy: Interruption of soil-transmitted helminth transmission Less than 1% overall soil-transmitted helminth infection prevalence in all risk groups • Endpoint: measurable endpoint, indirect indicator of morbidity• Parasitologic monitoring: intense monitoring and evaluation required• Platform: integrated or community-based platform required• Water, sanitation, and hygiene: more intense integration required• Cost: most expensive• Research: operational research required Several specific aspects underscore the importance of the choice of one common strategy for soil-transmitted helminthiasis control. For example, it is generally acknowledged that soil-transmitted helminth infection negatively impacts health, especially when infection intensity is high; that safe and effective anthelmintic drugs are available to reduce morbidity; and that preventive chemotherapy is an effective way to reach those at risk. However, a recent Cochrane review [59] and a systematic review with network meta-analysis [60], while criticized for their methodologic limitations and other concerns [61,62], challenged some of the portrayed beneficial effects. The Committee advocates for rigorous parasitologic monitoring after several rounds of preventive chemotherapy to assess the reduced burden of moderate- and high-intensity infections associated with morbidity, enabling a more accurate quantification of the likely health benefits of deworming. Indeed, a return from a treatment coverage target to the original goal of eliminating soil-transmitted helminthiasis as a public health problem, and the prioritization of parasitologic monitoring would offer a measurable and direct endpoint for national programs (i.e., less than 1% moderate or heavy infection intensity prevalence in all risk groups). At present, it remains unclear whether this goal can be reached through preventive chemotherapy alone. It is also important to note that sustaining the gains against soil-transmitted helminthiasis made possible by community-based GPELF programs will not be feasible without taking the goal of eliminating soil-transmitted helminthiasis as a public health problem seriously, as monitoring is needed to guide the planning of a transition from lymphatic filariasis elimination to soil-transmitted helminthiasis control. At present, drug coverage in the 3 identified high-risk groups alone is too often the main focus. It may be that other at-risk groups (e.g., adolescents and adults) constitute an important reservoir of transmission, which may need specific control efforts. Accounting for these populations will more accurately reflect the success of a control program [63]. The interruption of soil-transmitted helminthiasis transmission is a topic of growing interest [64,65]. History shows that sustained control efforts, coupled with economic development, can lead to transmission interruption in different parts of the world [66–68]. However, the attributable preventive fraction of different control strategies for successful transmission interruption is difficult to assess, and many experts emphasized that urbanization, economic development, and improved hygiene are more important factors than repeated anthelmintic treatment because rapid reinfection occurs frequently in highly endemic areas. As it is unlikely that such rapid and sustained economic developments will occur anytime soon in many of the most affected low-income countries, this underscores the importance of additional tools for control efforts. Yet, mathematical modeling also suggests that interruption of transmission is feasible in soil-transmitted helminthiasis–endemic settings that are characterized by low-infection intensities [65]. The burden of soil-transmitted helminthiasis varies across settings. A multifaceted, intersectoral approach along with appropriate delivery platforms is needed to achieve the ambitious goal of interrupting soil-transmitted helminthiasis transmission at a local level. WHA 54.19 originally called for improved access to WASH through intersectoral collaboration. Growing evidence supports that call [69] and further pleas for WASH integration into neglected tropical disease control programs have been re-emphasized [70]. While WHO has begun to integrate WASH into its global neglected tropical disease control strategy [71], guidelines are needed for the implementation of specific WASH interventions into soil-transmitted helminthiasis control strategies, similar to that of the “SAFE” strategy targeting trachoma [72–74]. Vast resources have been contributed to sustain and expand programs for the 10 neglected tropical diseases highlighted in the London Declaration to be eradicated, eliminated, or controlled by 2020. While many programs registered success due to this collaborative effort [75,76], guidelines for the evaluation of soil-transmitted helminthiasis control programs need to be strengthened. The Committee advocates that parasitologic surveys need to be performed after several years of preventive chemotherapy to document whether or not the goals set by WHO (i.e., those pertaining to infection intensity) have been achieved. Suitable approaches (e.g., adequately powered surveys) need to be included in a revised WHO strategic plan. The key recommendations put forth by the Committee are summarized in Box 1. Box 1. Key items, related challenges, and recommendations to all stakeholders put forth by the Soil-Transmitted Helminthiasis Advisory Committee (“the Committee”) at the 2016 annual meeting with regard to global control efforts for soil-transmitted helminthiasis Key item 1: Elimination of soil-transmitted helminthiasis as a public health problem Challenge: While elimination as a public health problem is clearly defined (<1% prevalence of moderate- or heavy-intensity infections for any soil-transmitted helminth species in a distinct geographic area), there is disagreement on the tools needed to achieve and to assess elimination. Recommendation: The Committee supports this definition of soil-transmitted helminthiasis elimination and urges all stakeholders to develop a common strategy on how to achieve this goal. Key item 2: Parasitologic monitoring of control efforts Challenge: Accurate parasitologic studies are not carried out on a regular basis in many endemic areas. There is no agreement on a sampling design to determine if set targets have been reached. Recommendation: Parasitologic monitoring in endemic countries is essential for assessing progress toward the elimination goal. WHO should develop and support a sampling design that is powered enough to determine if the goal of <1% prevalence of moderate- or heavy-intensity infection has been reached and affordable and relatively easy to implement given the limited resources available to, and capacity of, national control programs. The reporting of age- and sex-disaggregated data should be emphasized. Key item 3: Anthelmintic treatment coverage of at-risk groups Challenge: Anthelmintic treatment rates for preschool-aged children (PSAC) lag behind coverage rates reported for school-aged children (SAC), while most women of reproductive age (WRA) remain untreated amid scale-up efforts in high-burden countries. Recommendation: Conduct operational research to identify challenges for coverage of PSAC and WRA and use findings for developing new guidelines for these risk groups. Key item 4: Reporting on treatment coverage and data sharing on subnational level Challenge: WRA are among the at-risk groups for whom deworming is recommended, but treatment coverage data are not reported. For all groups receiving treatment, it would be more informative to have regional- and/or district-specific coverage rates in addition to national estimates. Recommendation: WHO should improve reporting of treatment coverage rates by inclusion of WRA in the regular updates on soil-transmitted helminthiasis published in the Weekly Epidemiological Record (WER). Additionally, WHO can provide a platform where subnational-level data on drug coverage in soil-transmitted helminthiasis–endemic districts should be shared whenever available. It is further suggested that WHO report the proportion of soil-transmitted helminthiasis–endemic districts (globally and by country) that have reached at least 75% coverage. Key item 5: Water, sanitation, and hygiene (WASH) Challenge: WASH is essential for soil-transmitted helminthiasis elimination as a public health problem and more investment is needed to include this important component into control efforts. Recommendation: Long-term investments for soil-transmitted helminthiasis–specific WASH are needed, and WASH indicators should be included in the London Declaration Scorecard that align with the 2030 Sustainable Development Goal (SDG) 6, that is to “ensure availability and sustainable management of water and sanitation for all”. Key item 6: Transition from lymphatic filariasis elimination to soil-transmitted helminthiasis control Challenge: Many ancillary benefits of the Global Program for Eliminating Lymphatic Filariasis (GPELF) with regard to soil-transmitted helminthiasis might be lost if GPELF is scaled down. Recommendation: Design an effective transition strategy and conduct operational research to identify and promote the policy frameworks, capacity building, planning, and intersectoral collaboration needed to sustain the contributions of the lymphatic filariasis program to progress made in soil-transmitted helminthiasis control. Key item 7: Clinical morbidity due to soil-transmitted helminthiasis Challenge: Soil-transmitted helminths cause primarily chronic, subtle morbidity, which is difficult to assess. For an accurate estimation of the attributable disease burden, clinical studies are needed. Recommendation: Gather scientific evidence pertaining to clinical morbidity due to soil-transmitted helminthiasis and address how soil-transmitted helminthiasis control activities may lead to a measurable decrease of morbidity in endemic areas. Key item 8: Laboratory diagnosis of soil-transmitted helminthiasis Challenge: The global implementation of standard diagnostic tools based on microscopy (i.e., Kato-Katz technique) allowed comparison between countries, but these are not sensitive enough to be used in settings where elimination of soil-transmitted helminthiasis seems feasible and where infection intensities are low. Recommendation: Continue the development and validation of recent advances in PCR-based diagnostics for soil-transmitted helminthiasis and conduct rigorous, multisite evaluations, and strategic developments for larger-scale application in the field. Key item 9: Combination therapy for soil-transmitted helminthiasis Challenge: Preventive chemotherapy programs have increased considerably worldwide. Yet no single drug is equally effective in achieving satisfactory cure rates for the major soil-transmitted helminths, and drug resistance is expected to arise and further decrease the efficacy of available treatment options. Recommendation: The Committee appreciates both the efforts and challenges to developing coformulations of anthelmintic drugs and supports research initiatives that assess the safety and efficacy of various combination therapies in order to identify which combination is best suited for scaling up to achieve a maximum impact. Key item 10: Ownership of soil-transmitted helminthiasis control programs Challenge: Drug donation is the cornerstone of current soil-transmitted helminthiasis control efforts in many areas, but this is not a sustainable solution without a long-term perspective. Recommendation: Country ownership of soil-transmitted helminthiasis prevention and control programs is paramount, and future efforts should not rely on drug donation alone. Generic deworming drugs will become increasingly important post-2020, and WHO should encourage the prequalification of the manufacturers of these drugs. Key item 11: Foci of continued soil-transmitted helminthiasis transmission Challenge: Guidance is required on how to deal with foci of ongoing transmission in areas where a regular preventive chemotherapy program is no longer being implemented. Recommendation: WHO should develop or endorse decision-making guidelines for program managers to identify and respond to foci of “unexpectedly high” soil-transmitted helminthiasis transmission post-preventive chemotherapy program.

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          Most cited references73

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          Disease and Development: Evidence from Hookworm Eradication in the American South.

          This study evaluates the economic consequences of the successful eradication of hookworm disease from the American South. The hookworm-eradication campaign (c. 1910) began soon after (i) the discovery that a variety of health problems among Southerners could be attributed to the disease and (ii) the donation by John D. Rockefeller of a substantial sum to the effort. The Rockefeller Sanitary Commission (RSC) surveyed infection rates in the affected areas (eleven southern states) and found that an average of forty percent of school-aged children were infected with hookworm. The RSC then sponsored treatment and education campaigns across the region. Follow-up studies indicate that this campaign substantially reduced hookworm disease almost immediately. The sudden introduction of this treatment combines with the cross-area differences in pre-treatment infection rates to form the basis of the identification strategy. Areas with higher levels of hookworm infection prior to the RSC experienced greater increases in school enrollment, attendance, and literacy after the intervention. This result is robust to controlling for a variety of alternative factors, including differential trends across areas, changing crop prices, shifts in certain educational and health policies, and the effect of malaria eradication. No significant contemporaneous results are found for adults, who should have benefited less from the intervention owing to their substantially lower (prior) infection rates. A long-term follow-up of affected cohorts indicates a substantial gain in income that coincided with exposure to hookworm eradication. I also find evidence that eradication increased the return to schooling.
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            Sensitivity of diagnostic tests for human soil-transmitted helminth infections: a meta-analysis in the absence of a true gold standard

            1 Introduction Reliable, sensitive and practical diagnostic tests are an essential tool in disease control programmes, including those for neglected tropical diseases. The requirements and expectations for a diagnostic tool in terms of technical performance, feasibility and costs change as control programmes progress through different phases, from initially high levels of infections to the confirmation of absence of infections. More precisely, during initial mapping to identify priority areas for control, when infection levels are typically highest, a diagnostic test with moderate sensitivity is acceptable, although the chosen tool needs to be easy to use, cost-effective and allow for the high-throughput screening of large populations (McCarthy et al., 2012; Solomon et al., 2012). Since mapping data can also serve as a baseline for the monitoring and evaluation of programme impact, diagnostic tests must have sufficient performance to detect changes in the prevalence and intensity of infection (Solomon et al., 2012). In later stages of programmes, when infection prevalence and intensity have decreased significantly, more sensitive diagnostic tools are needed to establish an endpoint of treatment programmes. If test sensitivity is insufficient at this point, light infections might be missed and this runs the risk of stopping control programmes too early, before programme endpoints have been achieved. Highly sensitive tests are also required for surveillance once treatment has been stopped to detect the potential re-occurrence of infections (McCarthy et al., 2012; Solomon et al., 2012). Finally, diagnostic tests play an important role in the assessment of treatment efficacy (Albonico et al., 2012) and in patient management. For the detection of the human soil-transmitted helminth (STH) species, Ascaris lumbricoides, Trichuris trichiura and the hookworms (Necator americanus and Ancylostoma duodenale), The World Health Organization (WHO) currently recommends the use of the Kato-Katz method, based on duplicate slides (WHO, 2002). Other commonly used methods include direct smear microscopy, formol-ether concentration (FEC), McMaster, FLOTAC and Mini-FLOTAC. All of these techniques rely on visual examination of a small sample of stool to determine the presence and number of STH eggs (WHO, 1994). Due to intra- and inter-sample variation in egg counts (Booth et al., 2003; Krauth et al., 2012), microscopy-based techniques can have differing sensitivities, especially in low transmission settings. Moreover, diagnostic methods vary considerably in the quantification of egg counts, which is necessary to establish intensity of infection and to evaluate treatment effects (Knopp et al., 2011; Albonico et al., 2012; Levecke et al., 2014). In order to better understand the suitability of diagnostic tools for various transmission settings and stages of disease control programmes, we performed a meta-analysis of the most commonly used copro-microscopic STH diagnostic tests. Our main study objective was an independent and global assessment of the relative performance of commonly used diagnostic methods for STH, as well as factors associated with heterogeneity in test sensitivity. Previous evaluations of STH diagnostics have generally relied on comparisons with a combined reference standard (generated by adding the results of several compared tests or consecutively obtained samples), an approach which has been widely criticised (Enoe et al., 2000; Ihorst et al., 2007). Moreover, the absence of a common reference standard has been a major obstacle for combined evaluations of diagnostic tests in the form of a meta-analysis. We have addressed this problem by using Bayesian latent class analysis (LCA), which allows simultaneous estimation of the unknown true prevalence of infection and the sensitivities and specificities of compared diagnostic tests. This approach has been previously applied to the evaluation of imperfect diagnostic tests for Chagas disease, leishmaniasis and malaria (Menten et al., 2008; de Araujo Pereira et al., 2012; Goncalves et al., 2012), as well as specific studies evaluating STH diagnostic methods (Booth et al., 2003; Tarafder et al., 2010; Assefa et al., 2014; Knopp et al., 2014). The approach has also been used for the meta-analyses of diagnostic test performance (Ochola et al., 2006; Menten et al., 2008; Limmathurotsakul et al., 2012). The current paper presents a Bayesian meta-analysis of different diagnostic tests for the detection of STH species. 2 Materials and methods 2.1 Literature search A systematic literature search was performed to identify publications presenting the evaluation of diagnostic techniques for the human STH species, A. lumbricoides, T. trichiura and hookworms (N. americanus and A. duodenale). Systematic searches were performed (date of search 25th February 2014) using the electronic databases PubMed (http://www.ncbi.nlm.nih.gov/), MEDLINE and EMBASE (via OvidSP) (http://ovidsp.uk.ovid.com/) and the medical subject headings and search terms as detailed in Supplementary Data S1. Articles were considered if written in English, German, French or Spanish. The search was validated by verifying that a number of previously identified key readings were included in the retrieved search results. The titles of initially obtained search results were screened for suitable content and all abstracts mentioning studies on helminths were retrieved. The abstracts were subsequently screened for studies using more than one diagnostic test for the determination of infections, even if not directly mentioning a comparison of test performances. Full texts were read and information on test outcomes, egg counts, age-groups, countries of the studies and years of publication was extracted where results were presented in a suitable format as explained below. Reference lists were screened for additional publications. The literature selection process is outlined in Fig. 1. Data were collected separately for A. lumbricoides, T. trichiura and hookworms, and restricted to the most commonly used diagnostic methods for STH, namely Kato-Katz (Katz et al., 1972), direct microscopy (WHO, 1994), formol-ether concentration (FEC) (Ritchie, 1948), McMaster (Ministry of Agriculture Fisheries and Food, 1986), FLOTAC (Cringoli et al., 2010) and Mini-FLOTAC (Barda et al., 2013a). Other techniques such as midi-Parasep, Koga Agar Plate, Willis technique and Spontaneous tube sedimentation technique (SSTT) were not included due to a lack of suitable data. As performance during field surveys was the main interest, evaluations of diagnostic tests on samples from diagnostic laboratories of hospitals were excluded. Only data provided in the form of 2 × 2 comparisons (T1+T2+, T1+T2−, T1−T2+, T1−T2−, where T1 and T2 are the two diagnostic methods and + and − indicate the observed positive or negative results) were retained. This also included data for which these 2 × 2 comparisons could be created by transforming the original data provided, e.g. where comparisons were made against a combined ‘gold standard’ of two diagnostic methods. Additionally, data on egg counts obtained by the various techniques were retrieved, including those studies that did not provide data in a suitable format for the LCA. Arithmetic mean egg counts were the most commonly reported measures and therefore used for the analysis. For articles where data could not be directly extracted, corresponding authors were invited to contribute additional study results. Three authors replied and provided four datasets for the analysis; we were also able to contribute a further two datasets to the analysis. 2.2 Bayesian LCA A Bayesian latent class model was used to estimate the sensitivity of different diagnostic tests as described elsewhere (Dendukuri and Joseph, 2001; Branscum et al., 2005). LCA allows estimation of the sensitivity and specificity of imperfect diagnostic tests by assuming a probabilistic model for the relationship between five unobserved, or latent, parameters: true disease prevalence π k and the sensitivities S i , S j and specificities C i , C j of diagnostic methods i and j (Pepe and Janes, 2007). The model additionally incorporates the covariance terms covD ij + , covD ij - to account for conditional dependency between compared diagnostic tests amongst infected and non-infected individuals, which is necessary as the included diagnostic tests are based on the same biological principle (detection of eggs under a microscope) and therefore factors other than the true infection status are likely to influence both test outcomes simultaneously (Dendukuri and Joseph, 2001). Thus, the joint distribution of the results of a 2 × 2 table follows a multinomial distribution, ( X k + + , X k + - , X k - + , X k - - ) ∼ Multi ( p k + + , p k + - , p k - + , p k - - , N k ) with the multinomial probabilities calculated as follows: p k + + = P ( T i + , T j + | k th population ) = [ S i S j + covD ij + ] π k + [ ( 1 - C i ) ( 1 - C j ) + covD ij - ] ( 1 - π k ) p k + - = P ( T i + , T j - | k th population ) = [ S i ( S j - 1 ) - covD ij + ] π k + [ ( 1 - C i ) C j - covD ij - ] ( 1 - π k ) p k - + = P ( T i - , T j + | k th population ) = [ ( S i - 1 ) S j - covD ij + ] π k + [ C i ( 1 - C j ) - covD ij - ] ( 1 - π k ) p k - - = P ( T i - , T j - | k th population ) = [ ( S i - 1 ) ( S j - 1 ) + covD ij + ] π k + [ C i C j + covD ij - ] ( 1 - π k ) The conditional correlations between two test outcomes for infected and non-infected individuals were calculated as ρ D + = covD + S i ( 1 - S i ) S j ( 1 - S j ) and ρ D - = covD - C i ( 1 - C i ) C j ( 1 - C j ) , respectively. Uninformative prior information was provided for the sensitivity and underlying true prevalence (using a beta distribution with the shape parameters alpha and beta equal to 1). For the covariance terms, a uniform prior distribution was assumed with limits as described in Dendukuri and Joseph (2001) and Branscum et al. (2005) to ensure that probabilities are confined to values between 0 and 1. Specificity was included as a fixed term based on the most parsimonious, best-fitting model (i.e. that with the lowest deviance information criterion (DIC) value) and was assumed to be the same for all compared methods. This was justified on the dual assumption that false positives are rarely obtained by any type of copro-microscopic technique (Knopp et al., 2011; Levecke et al., 2011) and the necessity to restrict the number of estimated parameters for the identifiability of the model. The models, built separately for A. lumbricoides, T. trichiura and hookworms, were computed using WinBUGS software version 14 (Spiegelhalter, D., Thomas, A., Best, N., Gilks, W., 1996. BUGS: Bayesian Inference Using Gibbs Sampling. MRC Biostatistics Unit, Cambridge). Models were also developed separately for low and high intensity settings. Stratification was based on reported arithmetic mean egg counts (in eggs per gram of faeces, epg). Empirical cut-offs of 2500 epg, 400 epg and 165 epg average infection intensity were used for A. lumbricoides, T. trichiura and hookworms, respectively. These cut-offs were established based on the overall average infection intensity of studies included in the meta-analysis. Data with only geometric means reported were excluded from this analysis unless the geometric mean, which is lower than the average egg count, exceeded the cut-off value. Further details of model parameterisation, including handling of multiple slides, are provided in Supplementary Data S2. 2.3 Comparison of quantitative performances To compare the various diagnostic tests in terms of their quantitative performance, we compared the arithmetic mean egg count obtained by various techniques. Statistical significance of differences was assessed using the non-parametric paired Wilcoxon signed-ranks test and the linearity of the relationship between counts was assessed by scatter plots of log-transformed (natural logarithm) average egg counts. Moreover, we evaluated the percentage of studies reporting egg counts of other techniques that were lower/higher than the Kato-Katz method, which currently forms the basis of the WHO defined intensity thresholds. To allow for a small variation in counts, egg counts were considered as lower or higher than the Kato-Katz method if these were lower or higher than the Kato-Katz egg count plus or minus 10%. Due to the limited availability of data and the fact that faecal egg counts do not vary significantly by the sampling effort for Kato-Katz analysis, all versions of Kato-Katz were combined (Levecke et al., 2014). 3 Results 3.1 Identification of diagnostic test comparisons The initial literature search identified 56 articles which were retrieved for full-text review. Of these, 32 studies fulfilled the inclusion criteria and 2 × 2 comparison data could be obtained for 20 studies (Table 1) (see Fig. 1 for an outline of literature selection steps). The number of extracted 2 × 2 comparisons by species and diagnostic methods is shown in Fig. 2. The included studies were published between 2003 and 2014 and conducted in 12 countries, primarily among school-aged children. The inclusion of only recent studies was somewhat surprising. Even though the original literature search had retrieved studies published since 1967, the non-availability of 2 × 2 data, the type of compared techniques and the evaluation of methods in laboratory or hospital samples led to their exclusion. The evaluation of diagnostic tests was mainly based on comparison with a combined reference-standard (14 of 20 studies); few studies used predicted estimates as a reference (1/20), an LCA approach (1/20) or a combination of the two (1/20). Three studies did not provide sensitivity estimates. The most widely applied method was the Kato-Katz method in 18 of 20 studies (mostly 1-slide or 2-slides on a single sample). The main characteristics of included studies are summarised in Table 1. 3.2 LCA of diagnostic test sensitivities (presence of infection) For all STH species, the models allowing for dependency between compared diagnostic tests showed a better fit, indicated by a lower DIC (not shown). Significant positive correlation between diagnostic test outcomes for infected individuals was observed, especially for comparisons of a 1-slide 1-sample Kato-Katz test with other diagnostic tests (details are provided in Supplementary Data S2). Taking this dependency into account, the sensitivities of selected diagnostic methods were estimated separately for A. lumbricoides, T. trichiura and hookworm and are provided in Table 2 and Fig. 3. Generally, sensitivities of all compared tests were higher for T. trichiuria (Fig. 3B) than for hookworm (Fig. 3C) and A. lumbricoides (Fig. 3A). The obtained sensitivities were highest overall for the FLOTAC method with 79.7% (95% Bayesian credible interval (BCI): 72.8–86.0%), 91.0% (95% BCI: 88.8–93.5%), and 92.4% (95% BCI: 87.6–96.2%) for A. lumbricoides, T. trichiura and hookworm, respectively (Table 2). The lowest sensitivity was observed for the direct microscopy method with 52.1% (95% BCI: 46.6–57.7%), 62.8% (95% BCI: 56.9–68.9%), and 42.8% (95% BCI: 38.3–48.4%), respectively. The estimated sensitivity of the 2-slide 1-sample Kato-Katz test for A. lumbricoides was 64.6% (95% BCI: 59.7–69.8%), for T. trichiura was 84.8% (95% BCI: 82.5–87.1%) and for hookworm was 63.0% (95% BCI: 59.8–66.4%). These estimates were only a slight improvement upon the sensitivities of a 1-slide 1-sample Kato-Katz test. However, increased sensitivities could be observed for 1-slide Kato-Katz performed on two consecutive samples. The sensitivity for Kato-Katz tests performed on three consecutive samples was only slightly further improved. Test specificities were not the main outcome and were fixed at 99.6% for A. lumbricoides, 97.5% for T. trichiura and 98.0% for hookworm, based upon model fit. 3.3 Effect of infection intensity on diagnostic test sensitivity The obtained sensitivity estimates by intensity group are presented in Table 3 and Fig. 4. For all tests and STH species evaluated in both intensity groups, sensitivity varied markedly and most strongly for the Kato-Katz method. For example, for A. lumbricoides the 1-slide Kato-Katz method had a sensitivity of 48.8% (95% BCI: 37.6–58.2%) in the low intensity group compared with 95.8% (95% BCI: 91.8–98.5%) in the high intensity group. Interestingly, in the low intensity group the sensitivity of Kato-Katz was improved markedly by performance of a second slide on the same sample. The sensitivity of the FLOTAC method was highest at 81.8% (95% BCI: 65.5–90.3%) at low intensity compared with 97.1% (95% BCI: 93.1–99.7%) at high intensity. 3.4 Comparison of quantitative test performances A total of 17, 16 and 27 comparisons of average Kato-Katz A. lumbricoides, T. trichiura and hookworm egg counts with other diagnostic methods were obtained from 11 articles (Table 1, analysis 2). The majority of comparisons were between versions of Kato-Katz and FLOTAC or McMaster techniques. Only a few studies compared egg counts between Kato-Katz and FEC or Mini-FLOTAC methods; none with direct microscopy. Table 4 shows that the FLOTAC method generally underestimates the average egg counts compared with Kato-Katz, even though the difference is not statistically significant for T. trichiura. The McMaster technique, however, resulted in a higher egg count for six of 11 comparisons (55%) for T. trichiura and four of 12 comparisons (33%) for hookworm whilst A. lumbricoides egg counts were significantly lower. The relationships between the logarithmic average measurements of Kato-Katz and FLOTAC or McMaster techniques followed a linear trend as shown by the scatter plots presented in Fig. 5. 4 Discussion A global assessment of STH diagnostic test sensitivities and their extent of variation is required to investigate the suitability of diagnostic tools for different transmission settings or stages of STH control programmes. Here we present, to our knowledge, the first meta-analysis of STH diagnostic method performance using a Bayesian LCA framework to overcome the absence of a true gold standard (Dendukuri and Joseph, 2001; Branscum et al., 2005). Our results demonstrate that sensitivities of evaluated diagnostic tests are low overall and cannot be generalised over different transmission settings. Sensitivity, overall and in both intensity groups, was highest for the FLOTAC method, but was comparable for Mini-FLOTAC and Kato-Katz methods. Test sensitivities are strongly influenced by intensity of infection and this variation needs to be taken into account for the choice of a diagnostic test in a specific setting. Moreover, reduced test sensitivity at low infection intensities is of increasing importance as ongoing control programmes reduce the prevalence and intensity of STH infections within endemic communities. The Kato-Katz method is the most widely used and reported diagnostic method, due to its simplicity and low cost (Katz et al., 1972), and is recommended by the WHO for the quantification of STH eggs in the human stool (WHO, 2002). Even though the overall sensitivity of the Kato-Katz method was low, the results of the stratified analysis suggest a high sensitivity of 74–95% when infection intensity is high, which is likely the case for mapping and baseline assessment. However, the test sensitivity dropped dramatically in low transmission settings, making the method a less valuable option in later stages of control programmes. This is likely a reflection of methodological problems specific to the Kato-Katz method, especially when diagnosing multiple STH species infections, as different helminth eggs have different clearing times (Bergquist et al., 2009). In high intensity settings, little value was added by performing a 2-slide test on the same sample, even though this is the currently recommended protocol; whereas in low intensity settings sensitivity was improved by performing a second slide. Sensitivity increased significantly when performing the Kato-Katz method on multiple consecutive samples, which is most likely explained by daily variations of egg excretions and the non-equal distribution of eggs in the faeces leading to substantial variation in egg numbers between stool samples from the same person (Booth et al., 2003; Krauth et al., 2012). For all investigated STH species, sensitivity was highest for the FLOTAC method, even when evaluated in low intensity settings, a finding which is consistent with previous evaluations (Utzinger et al., 2008; Knopp et al., 2009b; Glinz et al., 2010). However, despite its improved performance compared with other copro-microscopic methods, FLOTAC has several practical constraints including higher associated costs, necessity of a centrifuge and longer sample preparation time, decreasing its value as a universal diagnostic method (Knopp et al., 2009a). To enable its use in settings with limited facilities, the Mini-FLOTAC method, a simplified form of FLOTAC, was developed (Barda et al., 2013a). Our findings suggest that the sensitivity of Mini-FLOTAC is much lower than FLOTAC, and it does not outperform the less expensive Kato-Katz method according to a recent study in Kenya (Speich et al., 2010; Assefa et al., 2014). A recognised advantage of the Mini-FLOTAC method, however, is that it can be performed on fixed stools, enabling processing at a later date in a central laboratory. This can help to increase the quality control process and overcomes some of the logistical difficulties in examining fresh stool samples in the field on the day of collection (Barda et al., 2013a). The obtained Mini-FLOTAC sensitivity estimates have relatively high uncertainty, visible in the wide confidence intervals, probably due to the limited number of studies available for the analysis and their evaluation primarily in low transmission settings, where the number of positive individuals is very limited. The detection or failure of detection of a single individual therefore might have a large impact on the sensitivity estimate. In remote areas where microscopy is often unavailable, studies can also use FEC, which allows the fixation of stool samples for later examination (WHO, 1994); several authors have also suggested the use of the McMaster technique as it is easier to standardise than Kato-Katz (Levecke et al., 2011; Albonico et al., 2012). Overall, the observed relative performances of these diagnostic tests when compared with the Kato-Katz method are consistent with those presented in the literature: the performance of Kato-Katz and McMaster methods were comparable, although this did vary by setting (Levecke et al., 2011; Albonico et al., 2013). Similarly, even though FEC had predominantly lower sensitivity than Kato-Katz in included studies, the reported relative performance varies in the literature (Glinz et al., 2010; Speich et al., 2013). The sensitivity of direct microscopy was consistently lower than the Kato-Katz method. Other available methods which were not included in our meta-analysis due to limited data availability, such as the midi-Parasep, do not show any improved test performance in their previous evaluations (Funk et al., 2013). Although we present an improved approach for evaluating diagnostic test performances, accounting for the absence of a perfect gold standard by estimating the true unmeasured infection status and allowing for conditional dependency between the test outcomes, our analysis is subject to several limitations. The results presented here are limited by the low availability of comparable data for each diagnostic test, especially when performing the analysis stratified by intensity group. Direct microscopy was primarily evaluated in low intensity settings, which could have led to the lower observed sensitivity estimates, whereas the Kato-Katz method was evaluated in a full range of settings. The cut-off value to define high and low intensity groups of study populations was chosen based on the data included in the meta-analysis, but does not necessarily represent two main types of transmission settings. Nevertheless, the groupings demonstrate the substantial differences in test performance across varying infection intensities. As the investigated range of transmission settings was limited, further diagnostic test evaluations in specified transmission settings will be needed to provide concrete test performance estimates for each of the settings. To take into account the conditional dependency between compared diagnostic tests, we used a fixed effects model, assuming that conditional dependency is the same for all study settings. Different approaches allowing for varying correlations by using random effects to model sensitivities and specificities as a function of a latent subject-specific random variable could be explored further (Dendukuri and Joseph, 2001). Moreover, our findings might be biased towards results from studies comparing multiple diagnostic tests at the same time, as these are underpinned by a larger amount of data. Assumptions had to ensure identifiability of the model by limiting the number of parameters to be estimated. We focussed our analysis on the sensitivity of diagnostic tests, assuming that specificity of various methods do not differ largely, and therefore included the specificity of all single sample diagnostic tests as one fixed parameter. This assumption can be questioned, as for example Kato-Katz slides are more difficult to read than FLOTAC slides due to debris (Glinz et al., 2010); however, it is still an improvement on the assumption of 100% test specificity for all diagnostic tests as applied in previous publications (Booth et al., 2003; Knopp et al., 2011; Levecke et al., 2011). Using uninformative priors instead of fixed terms did not improve model fit and led to slightly wider BCIs. Importantly, the current model assumes that sensitivities are identical within all populations, which is not fulfilled if sensitivity varies by study setting (Toft et al., 2005). Indeed, the stratified analysis showed that sensitivity varied by infection intensity; however, there were not sufficient data to obtain good estimates for all tests in various transmission settings. Additionally, sensitivity in a specific study setting might be affected by other factors including stool consistency and diet, standardisation and adherence to protocols, equipment quality and human error (Bogoch et al., 2006; Bergquist et al., 2009; Levecke et al., 2011). To overcome the limited comparability of evaluations from different studies, purposeful evaluations of test sensitivity over a continuous range of infection intensities in comparable populations, for example before and after treatment rounds, are clearly necessary to better refine sensitivity estimates, and could be used to identify intensity categories within which sensitivity remains comparable. Results could then be transformed into recommendations for the use of diagnostic tests for different stages of disease control programmes. The performance of a diagnostic tool should not only be measured in terms of sensitivity, but also needs to consider the ability of the test to quantify faecal egg counts. Current infection and treatment effect indicators are based on the Kato-Katz method, and the question arises whether the increasing use of other methods will constitute a problem for standardised recommendations (WHO, 2002). The comparison of average egg counts obtained by Kato-Katz and FLOTAC methods shows a broad agreement with previous studies with generally higher Kato-Katz egg counts (Knopp et al., 2009b, 2011; Albonico et al., 2013). The quantitative performance of the McMaster technique, however, varied in comparison to the Kato-Katz method as higher McMaster average egg counts were observed in several studies, especially for T. trichiura and hookworms (Levecke et al., 2011; Albonico et al., 2012, 2013). The current analysis has focussed on copro-microscopic diagnostic tests, which are based on examination of stool samples. There is current interest in developing more sensitive assays that allow a high sample throughput for screening of large populations using other biological samples and the simultaneous detection of several parasite species in co-endemic settings (Bergquist et al., 2009; Knopp et al., 2014). Recently, assays based on PCR have been developed for the detection of STH (Verweij et al., 2007; Schar et al., 2013; Knopp et al., 2014); however, we did not include this method in our meta-analysis due to limited data availability from field settings. Nonetheless, a recent study showed that the sensitivity of PCR methods was comparable with the Kato-Katz method, especially in low endemicity settings (Knopp et al., 2014). In conclusion, we provide a first known meta-analysis of the sensitivity and quantitative performance of STH diagnostic methods most widely used in resource-limited settings. Our results show that the FLOTAC method had the highest sensitivity both overall and in low intensity settings; however this technique requires a centrifuge and has relatively low throughput. Our results further show that the sensitivities of the Kato-Katz and Mini-FLOTAC techniques were comparable and in high intensity settings both techniques provide a practical and reliable diagnostic method. A particular advantage of the Kato-Katz method is the ability to simultaneously detect STH and schistosome species at low cost; whereas the Mini-FLOTAC method has the advantage that it can be used on preserved samples. As control programmes reduce the intensity of infection, there is a need for diagnostic methods which are more sensitive than these currently used. In evaluating the performance of new diagnostic methods we recommend a standardised evaluation in multiple transmission settings, using the robust statistical methods presented here, as well as a consideration of the cost-effectiveness of alternative methods (Assefa et al., 2014).
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              New diagnostic tools in schistosomiasis.

              Schistosomiasis is a water-based parasitic disease that affects over 250 million people. Control efforts have long been in vain, which is one reason why schistosomiasis is considered a neglected tropical disease. However, since the new millennium, interventions against schistosomiasis are escalating. The initial impetus stems from a 2001 World Health Assembly resolution, urging member states to scale-up deworming of school-aged children with the anthelminthic drug praziquantel. Because praziquantel is safe, efficacious and inexpensive when delivered through the school platform, diagnosis before drug intervention was deemed unnecessary and not cost-effective. Hence, there was little interest in research and development of novel diagnostic tools. With the recent publication of the World Health Organization (WHO) Roadmap to overcome the impact of neglected tropical diseases in 2020, we have entered a new era. Elimination of schistosomiasis has become the buzzword and this has important ramifications for diagnostic tools. Indeed, measuring progress towards the WHO Roadmap and whether local elimination has been achieved requires highly accurate diagnostic assays. Here, we introduce target product profiles for diagnostic tools that are required for different stages of a schistosomiasis control programme. We provide an update of the latest developments in schistosomiasis diagnosis, including microscopic techniques, rapid diagnostic tests for antigen detection, polymerase chain reaction (PCR) assays and proxy markers for morbidity assessments. Particular emphasis is placed on challenges and solutions for new technologies to enter clinical practice.
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                Author and article information

                Contributors
                Role: Editor
                Journal
                PLoS Negl Trop Dis
                PLoS Negl Trop Dis
                plos
                plosntds
                PLoS Neglected Tropical Diseases
                Public Library of Science (San Francisco, CA USA )
                1935-2727
                1935-2735
                14 August 2018
                August 2018
                : 12
                : 8
                : e0006606
                Affiliations
                [1 ] Swiss Tropical and Public Health Institute, Basel, Switzerland
                [2 ] University of Basel, Basel, Switzerland
                [3 ] Institute of Medical Microbiology and Hygiene, Saarland University, Homburg/Saar, Germany
                [4 ] Ateneo School of Medicine and Public Health, Ateneo de Manila University, Metro Manila, the Philippines
                [5 ] Children Without Worms, The Task Force for Global Health, Decatur, Georgia, United States of America
                [6 ] Rollins School of Public Health, Emory University, Atlanta, Georgia, United States of America
                [7 ] Soil-Transmitted Helminthiasis Advisory Committee, Decatur, Georgia, United States of America
                [8 ] Modibbo Adama University of Technology, Yola, Nigeria
                [9 ] College of Public Health, University of the Philippines, Manila, the Philippines
                [10 ] Department of Environmental Health, Emory University, Atlanta, Georgia, United States of America
                [11 ] Department of Epidemiology, Biostatistics, and Occupational Health, McGill University, Montreal, Quebec, Canada
                [12 ] Instituto de Investigaciones en Enfermedades Tropicales, Universidad Nacional de Salta, Oran, Argentina
                [13 ] Department of Virology, Parasitology, and Immunology, Faculty of Veterinary Medicine, Ghent University, Ghent, Belgium
                [14 ] Kenya Medical Research Institute, Nairobi, Kenya
                [15 ] London School of Hygiene and Tropical Medicine, London, United Kingdom
                Baylor College of Medicine, UNITED STATES
                Author notes

                The authors have declared that no competing interests exist.

                Author information
                http://orcid.org/0000-0003-3634-8802
                http://orcid.org/0000-0002-5609-3811
                http://orcid.org/0000-0002-1517-2572
                Article
                PNTD-D-18-00173
                10.1371/journal.pntd.0006606
                6091919
                30106975
                9492e0b4-20c3-47cb-b158-5a175059ba69
                © 2018 Becker 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.

                History
                Page count
                Figures: 0, Tables: 4, Pages: 17
                Funding
                The authors received no specific funding for this work.
                Categories
                Policy Platform
                Medicine and Health Sciences
                Parasitic Diseases
                Helminth Infections
                Medicine and Health Sciences
                Pharmaceutics
                Drug Therapy
                Chemotherapy
                Medicine and Health Sciences
                Parasitic Diseases
                Helminth Infections
                Soil-Transmitted Helminthiases
                Medicine and Health Sciences
                Tropical Diseases
                Neglected Tropical Diseases
                Soil-Transmitted Helminthiases
                Medicine and Health Sciences
                Health Care
                Health Statistics
                Morbidity
                Medicine and Health Sciences
                Parasitic Diseases
                Medicine and Health Sciences
                Public and Occupational Health
                Medicine and Health Sciences
                Health Care
                Environmental Health
                Sanitation
                Medicine and Health Sciences
                Public and Occupational Health
                Environmental Health
                Sanitation
                Medicine and Health Sciences
                Infectious Diseases
                Infectious Disease Control

                Infectious disease & Microbiology
                Infectious disease & Microbiology

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