Abstract
The objective of the review is to use individual participant data (IPD) meta-analysis to explore the effect of mass deworming during pregnancy. We developed a search strategy and searched the databases till March 2018. We included individually randomised controlled trials; cluster randomised controlled trials and quasi randomised studies providing preventive or therapeutic deworming drugs for soil transmitted helminthiases and schistosomiasis during pregnancy. All IPD were assessed for completeness, compared to published reports and entered into a common data spreadsheet. Out of the seven trials elgible for IPD, we received data from three trials; out of 8,515 potential IPD participants; data were captured for 5,957 participants. Findings from this IPD suggest that mass deworming during pregnancy reduces maternal anaemia by 23% (Risk ratio [RR]: 0.77, 95% confidence intreval [CI]: 0.73–0.81; three trials; 5,216 participants; moderate quality evidence). We did not find any evidence of an effect of mass deworming during pregnancy on any of the other outcomes. There was no evidence of effect modification; however these findings should be interpreted with caution due to small sample sizes. The quality of evidence was rated as moderate for our findings. Our analyses suggest that mass deworming during pregnancy is associated with reducing anaemia with no evidence of impact on any other maternal or pregnancy outcomes. Our analyses were limited by the availability of data for the impact by subgroups and effect modification. There is also a need to support and promote open data for future IPDs.
PLAIN LANGUAGE SUMMARY
Mass deworming during pregnancy reduces anaemia but has no effect on other maternal or pregnancy outcomes
Pregnant women are at particular risk from soil transmitted helminthiasis (STH) – a group of diseases caused by infection with four intestinal parasites. Individual-level data analysis with data from three studies shows that mass deworming during pregnancy reduces anaemia but has no effect on any other maternal or pregnancy outcomes.
What is this review about?
Soil transmitted helminthiasis (STH) are a group of diseases caused by infection with four intestinal parasites (two types of hookworm, roundworm, and whip worm) which contributed to a total of 4.98 million years lived with disability (YLDs) in 2010. Anaemia is one of the most common side effects of infection with STH or schistosomes, due to blood loss in the intestine or urinary tract. Women in low- middle-income countries (LMICs) are especially prone since they may be pregnant or lactating for as much as half of their reproductive lives with over 50% of the pregnant women having iron-deficiency anaemia.
This review explores whether the effect of mass deworming during pregnancy varies with individual characteristics (nutritional status, anaemia), intensity of infection (as assessed by egg count), infection status (including species of worm), socioeconomic status, sanitation environment and co-interventions. The analysis uses individual patient data (IPD), which means that the original individual-level data are obtained for the included studies and combined into a single data set.
What studies are included in this review?
Included studies have to be individually randomised controlled trials; cluster randomised controlled trials and quasi randomised studies providing preventive or therapeutic deworming drugs for STH and schistosomiasis during pregnancy.
From a total of 16 studies on mass deworming during pregnancy we identified seven trials with 8,515 participants were deemed to be eligible for individual data analysis. Of these seven trials, we received data from three trials so that out of 8,515 potential observations data were captured for 5,957.
What are the findings of this review?
Mass deworming during pregnancy reduces maternal anaemia by nearly one quarter (23%).
There is no effect of mass deworming during pregnancy on any of other outcomes including Trichiura infection, hookworm infection, low birthweight (LBW), and preterm birth.
The size of the effect is not affected by Trichiura intensity at baseline, maternal anaemia at baseline and maternal BMI at baseline. However these findings should be interpreted with caution due to small sample sizes. Other potential moderating characteristics could not be assessed because of lack of data.
The quality of evidence is rated as moderate for our findings. Further research on maternal baseline worm intensities and birth outcomes could change our findings.
What do the findings of this review mean?
The analyses suggest that mass deworming during pregnancy is associated with reducing anaemia with no effect on any other maternal or pregnancy outcomes. The analyses were limited by the availability of data for the impact by subgroups and effect modification and thus there is a need to assess mass deworming for STH and schistosomiasis during pregnancy in large scale programmatic settings along with an attempt to measure various individual and environmental factors that could potentially affect its impact. There is also a need to support and promote open data for future individual level data analysis.
EXECUTIVE SUMMARY/ABSTRACT
Background
Mass deworming is recommended as an effective strategy to prevent and treat soil transmitted helminthiases (STH) and schistosomiasis. However there is a great deal of heterogeneity in the existing evidence and the effectiveness of mass deworming in improving various maternal and newborn health outcomes is a current source of debate. Critical appraisal of existing studies suggests that these studies fail to account for various factors that could modify the effectiveness of deworming including nutritional status, type of infection, worm burden and concomitant interventions. Currently, it is difficult to establish whether mass deworming during pregnancy has beneficial effects under certain conditions and limited effects under others.
Objectives
The objective of the review is to use individual participant data (IPD) meta-analysis to explore whether the effect of mass deworming during pregnancy varies with individual characteristics (nutritional status, anaemia), intensity of infection (as assessed by egg count), infection status (including species of worm), socioeconomic status, sanitation environment and co-interventions.
Search methods
We developed a search strategy with an information scientist to search MEDLINE, CINAHL, LILACS, EMBASE, the Cochrane Library, Internet Documents in Economics Access Service (IDEAS), Google Scholar, Web of Sciences, Social Services Abstracts, WHO Global Health Library, Global Health CABI and CAB Abstracts till March 2018. We also searched grey literature, websites, contacted authors and screened references of relevant systematic reviews.
Selection criteria
We included individually randomised controlled trials; cluster randomised controlled trials and quasi randomised studies providing preventive or therapeutic deworming drugs for STH and schistosomiasis during pregnancy.
Data collection and analysis
We contacted all eligible study authors to invite them to join our investigators’ collaborative group and share their IPD. We used a data sharing agreement. All IPD were assessed for completeness, compared to published reports and entered into a common data spreadsheet. Risk of bias was assessed using the Cochrane Risk of Bias tool. Overall quality of the evidence was assessed using the Grading of Recommendations, Assessment, Development and Evaluations (GRADE) methods. This review was registered as a protocol in the Campbell Collaboration Library.
Results
We screened 23,406 records and identified a total of 16 studies on mass deworming during pregnancy; out of which seven trials with 8,515 participants were deemed to be eligible for IPD. Trial authors were contacted for all seven trials deemed eligible for the IPD. Out of the seven trials, we received data from three trials; data from two trails were lost (trialists were not able to retrieve the data); one trialist refused to share the data while one could not be contacted due to severe health conditions. In terms of the number of participants; out of 8,515 potential IPD participants; data was captured for 5,957 participants.
Findings from this IPD suggest that mass deworming during pregnancy reduces maternal anaemia by 23% (Risk ratio (RR): 0.77, 95% confidence intreval (CI): 0.73–0.81; three trials; 5,216 participants; moderate quality evidence). We did not find any evidence of an effect of mass deworming during pregnancy on any of other outcomes including Trichiura infection (RR: 0.69, 95% CI: 0.42–1.13; two trials; 2,867 participants; moderate quality evidence), hookworm infection (RR: 0.52, 95% CI: 0.18–1.47; two trials; 2,867 participants; moderate quality evidence), low birthweight (LBW) (RR: 0.89, 95% CI: 0.67–1.18; two trials; 2,267 participants; moderate quality evidence) and preterm birth (RR: 0.69, 95% CI: 0.47–1.03; two trials; 2,707 participants; moderate quality evidence). Due to limited availability of the data on the pre-defined effect modifiers, we could only assess for effect modification by baseline Trichiura infection, maternal anaemia at baseline and maternal body mass index (BMI) at baseline. There was no evidence of effect modification by Trichiura intensity at baseline, maternal anaemia at baseline and maternal BMI at baseline. However these findings should be interpreted with caution due to small sample sizes.
The quality of evidence is rated as moderate for our findings. Further research on maternal baseline worm intensities and birth outcomes could change our findings.
Authors’ conclusions
Our analyses suggest that mass deworming during pregnancy is associated with reducing anaemia with no impact on any other maternal or pregnancy outcomes. Our analyses were limited by the availability of data for the impact by subgroups and effect modification and thus there is a need to assess mass deworming for STH and schistosomiasis during pregnancy in large scale programmatic settings along with an attempt to measure various individual and environmental factors that could potentially affect its impact. There is also a need to support and promote open data for future IPDs.
Role of the funder
The Bill and Melinda Gates Foundation had no influence on the conclusions or publication.
BACKGROUND
The problem, condition or issue
Soil transmitted helminthiasis (STH) are a group of diseases caused by infection with four intestinal parasites: Ascaris lumbricoides (roundworm), Trichuris trichiura (whip worm), Necator americanus (hookworm) and Ancylostoma duodenale (hookworm). Schistosomiasis is also a parasitic disease caused by blood flukes of the genus Schistosoma. Six species of schistosomes are responsible for infection in humans: Schistosoma guineensis, Schistosoma haematobium, Schistosoma intercalatum, Schistosoma japonicum, Schistosoma mansoni and Schistosoma mekongi; S. haematobium and S. mansoni are predominant causes of disease. An estimated 438.9 million people were infected with hookworm in 2010, 819.0 million with roundworms and 464.6 million with whipworm. STH altogether, contributed to a total of 4.98 million years lived with disability (YLDs) (Pullan, Smith, Jasrasaria & Brooker, 2014). Of these YLDs, 65% were attributable to hookworm, 22% to roundworm and the remaining 13% to whipworm. In terms of geographical distribution, around 67% of STH occurred in Asia contributing to 68% of the YLDs (Pullan et al., 2014). Over 270 million preschool-age children and over 600 million school-age children live in STH endemic areas and an estimated 4 million pregnancies a year are complicated by maternal hookworm infection alone (Bundy, Chan & Savioli, 1995; WHO, 2005).
Anaemia is one of the most common side effects of infection with STH or schistosomes, due to blood loss in the intestine or urinary tract. Women in low- middle-income countries (LMICs) are especially prone since they may be pregnant or lactating for as much as half of their reproductive lives with over 50% of the pregnant women having iron-deficiency anaemia. Although iron-deficiency anaemia is multifactorial, hookworm infection is an important contributor in endemic areas, especially among women of reproductive age. An analysis on anaemia epidemiology based on data from the Global Burden of Diseases, Injuries and Risk Factors (GBD) 2010 study suggested that hookworm and Schistosomiasis were among the top ten causes of anaemia among females in 2010 (Kassebaum et al., 2014). It is the leading cause of pathological blood loss in tropical and subtropical regions (Pawlowski, Schad & Stott, 1991). Moreover there is a direct association between the intensity of STH infection, blood loss and consequent anaemia, especially for hookworms (Bundy et al., 1995; Chan, Medley, Jamison & Bundy, 1994; Larocque, Casapia, Gotuzzo & Gyorkos, 2005). The association between anaemia during pregnancy and adverse pregnancy outcomes, including low birth weight (LBW), preterm birth, perinatal mortality and infant survival has already been documented (Rahman et al., 2016; Sifakis & Pharmakides, 2000). Furthermore, the chances of favourable pregnancy outcomes are reduced by 30% to 45% in anaemic mothers, with their infants having less than one half of normal iron reserves (Rahman et al., 2016).
Mass deworming (treatment at a large scale irrespective of the diseases status) along with the water, sanitation and hygiene (WASH) interventions are generally accepted as effective measures to prevent and treat STH and Schistosomiasis. However, findings from existing studies are conflicting and the effectiveness of mass deworming in improving various maternal and child health outcomes is a current source of debate (Salam, Haider, Humayun & Bhutta, 2015; Turner et al., 2015). Critical appraisal of the existing studies suggests that these studies fail to account for various factors that could potentially modify the effectiveness of mass deworming including nutritional status, type of infection, worm burden and concomitant interventions (Barry, Simon, Mistry & Hotez, 2013; Turner et al., 2015).
The intervention
The World Health Organisation (WHO) recommends mass deworming (also called preventive chemotherapy, is the process of treating large numbers of people in areas with a high prevalence of these conditions) for STH and Schistosomiasis depending on prevalence of worm infection. Preventive chemotherapy (deworming), using single-dose albendazole (400 mg) or mebendazole (500 mg), is recommended as a public health intervention for pregnant women, after the first trimester, living in areas where both: the baseline prevalence of hookworm and/or Trichur trichiura infection is 20% or higher among pregnant women, and anaemia is a severe public health problem, with a prevalence of 40% or higher among pregnant women, in order to reduce the worm burden of hookworm and T. trichiura infection (WHO, 2017).
For Schistosomiasis, annual treatment with praziquantel in high risk communities (>50% prevalence) and once every 2 years in medium risk (>10% and <50% prevalence) is recommended and women can be treated with praziquantel at any stage of pregnancy and lactation (WHO, 2006). In addition to deworming; education on health and hygiene and provision of adequate sanitation is also recommended.
STH and Schistosomiasis are a major public health concern since these parasites feed on blood and affect the supply of nutrients necessary for erythropoiesis; hence contributing to anaemia (Hotez & Cerami, 1983; Torlesse & Hodges, 2000). Additionally, STH may also lead to haemorrhage by releasing anticoagulant compounds, thereby leading to iron-deficiency anaemia. Infection during pregnancy leads to an added demand for nutrients that are critical for foetal growth and development (Abrams & Miller 2011; Blackwell, Snodgrass, Madimenos & Sugiyama, 2010). Hookworms, in particular, along with other STH and schistosomes have been associated with reductions in haemoglobin and iron deficiency during pregnancy (Larocque et al., 2005; Gyorkos, Gilbert, Larocque & Casapía, 2011; Muhangi et al., 2007; Nurdia, Sumarni, Suyoko, Hakim & Winkvist, 2001; Ndyomugyenyi, Kabatereine, Olsen & Magnussen, 2008bb). Additionally, STH and Schistosomiasis often occur with co-infections in areas where malnutrition is already prevalent (Martin, Blackwell, Gurven & Kaplan, 2013).
Mass deworming is regarded as the most effective means of controlling mortality and morbidity with STH and Schistosomiasis (WHO, 2006, 2017). Preventive chemotherapy (either alone or in combination) has been used as a public heath tool for preventing morbidity due to infection usually with more than one helminth at a time since many of the antihelminthic drugs are broad spectrum. In 1994, the WHO convened an informal consultation on hookworm infection and anaemia in girls and women, which promoted the use of antihelminthics in pregnancy after the first trimester in areas where these infections are endemic and where anaemia is prevalent, but it also recommended evaluation of the long-term safety, particularly in terms of birth outcomes (WHO, 1994). Women can be treated with praziquantel for schistosomiasis at any stage of pregnancy and during lactation. Deworming during pregnancy is often accompanied with iron supplementation to reduce anaemia.
There are various factors that could potentially modify the effectiveness of mass deworming including baseline nutritional status (anaemia and body mass index [BMI]), type of STH infection, treatment protocol, worm burden (particularly intensity of infection) and concomitant interventions (such as iron supplementation and other drugs such as praziquantel for Schistosomiasis). However, given the limited number of studies assessing the impact of deworming on maternal and newborn health outcomes (Salam et al., 2015) and complex interactions between helminthic infections and immune function, health and co-infection risks (Blackwell, 2016), it is difficult to ascertain how these factors interplay. Currently, it is difficult to establish whether mass deworming during pregnancy has beneficial effects under certain conditions and limited effects under others and there exists a possibility that it is only beneficial in women with very high parasite burdens, dietary insufficiencies or both (Blackwell, 2016). Moreover, all intestinal worms are not the same; not all intestinal worms respond to the same deworming medication; and not all infested individuals exhibit the disease. Reinfection depends on the prevalence and intensity of infection as well as environmental factors such as the WASH practices in the community. Figure 1 highlights the logic model for this review.

Logic model [Color figure can be viewed at wileyonlinelibrary.com]
A Cochrane review on deworming in the second trimester of pregnancy including four trials and 4,265 participants concluded that there was insufficient evidence to recommend deworming in pregnancy (Salam et al., 2015). There was no impact of single dose of antihelminthics administered in the second trimester of pregnancy on maternal anaemia, LBW, preterm birth and perinatal mortality. A recent Campbell systematic review and network meta-analysis based on 47 randomised trials and over one million children, found little to no overall effect on growth, attention and school attendance (Welch et al., 2016). However, these reviews were conducted at the study level, rather than using data for each individual participant, which limits the power to detect effect modification by individual participant characteristics that could potentially modify the effect of deworming including baseline nutritional status, type of STH infection, treatment protocol, worm burden and concomitant interventions (such as iron supplementation; Barry et al., 2013; Turner et al., 2015).
IPD meta-analysis refers to analysing data for each participant in the existing studies (Tierney, Pignon et al., 2015; Tierney, Vale et al., 2015). The term IPD refers to analysing data recorded for each participant in contrast to the aggregate study data in meta-analysis. The advantage of an IPD analysis over aggregate meta-analysis is that it has the potential to improve the quality of both the data and the analyses and consequently the reliability of the results (Tierney, Vale et al., 2015). Furthermore, it also provides an opportunity to re-analyse the data for a range of other possibilities for example, investigating if the treatment effects varies by participant characteristics which is not possible with the aggregate data (Riley, Lambert & Abo-Zaid, 2010). An IPD approach will allow an evaluation of variation in effect estimates by various individual, socio-demographic and environmental factors among pregnant women that could potentially modify the effectiveness of mass deworming during pregnancy.
Despite the availability of more recent global estimates on the burden and interventions for STH and Schistosomiasis, additional research is needed to understand the factors that explain the variation in the effect estimates of recommended interventions to prevent transmission. Existing studies fail to account for various factors that could modify the effectiveness of mass deworming including underlying host and environment factors. IPD meta-analysis would explore the question of whether mass deworming during pregnancy is more effective for subgroups of women defined by characteristics such as nutrition status and infection intensity. This understanding could help develop targeted strategies to reach pregnant women with deworming and guide policy regarding mass deworming. A companion review using IPD and network meta-analysis to explore whether the effects of different types and frequency of deworming drugs as well as their combination with food or micronutrients vary with child-level and study-level characteristics is also registerd with Campbell Collaboration (Welch et al.).
Objectives
The objective of the review is to use IPD meta-analysis to explore whether the effect of mass deworming among pregnant women on maternal and birth outcomes vary with individual characteristics (nutritional status, anaemia), intensity of infection (as assessed by egg count), infection status (including species of worm), socioeconomic status, sanitation environment and other co-interventions.
METHODOLOGY
The protocol was registered with the Campbell Collaboration (Salam et al.) and reported according to the preferred reporting items for systematic reviews and meta-analyses for protocols (PRISMA-P) (Moher et al., 2015). Results of the review are reported using the Preferred Reporting items for Systematic Reviews and Meta-analyses of individual patient data (PRISMA-IPD) Statement (Stewart et al., 2015).
Criteria for including and excluding studies
We included studies that met the following eligibility criteria
Types of study designs
We included individually randomised controlled trials (RCT); cluster RCTs and quasi randomised studies (studies where non-random assignment is determined by factors that are out of the control of the investigator) as these were the most appropriate design for the IPD meta-analysis. No language or date restrictions were applied.
Types of participants
Participants were pregnant women receiving preventive or therapeutic deworming drugs for STH and schistosomiasis.
Types of interventions
We included mass deworming using any drug or a combination of drugs (including levamisole, mebendazole, albendazole, praziquantel and pyrantel) for STH and schistosomiasis with or without co-interventions compared to placebo or control (no mass deworming). Co-interventions could be food provision, micronutrient supplementation, iron and/or folic acid supplementation, hygiene interventions or education. We included studies where the co-interventions were similar in the intervention and control groups to assess the impact of mass deworming.
Types of outcome measures
Following primary and secondary outcomes were reported; however we did not use the list of outcomes as a criteria for inclusion of studies in the review:
Primary outcomes: Maternal anaemia at term (haemoglobin less than 11 g/dl) Maternal infection intensity (as reported by the study authors)
Secondary outcomes: Maternal haemoglobin at term Maternal ferritin Maternal anthropometric measures (height and weight) Maternal body mass index (BMI) Birth weight LBW (less than 2500 g) Preterm birth (birth before 37 weeks of gestation) Perinatal mortality (includes foetal death after 28 weeks of gestation and infant death that occurs at less than seven days of life) Stillbirth Congenital abnormalities Infant mortality
Duration of follow-up
We did not restrict inclusion based on the duration of follow-up.
Types of settings
The settings included any area where STH or schistosomes are endemic. These could include studies conducted in either community settings or facility settings including hospitals, antenatal clinics, primary healthcare centres etc.
Search strategy
We conducted the search in the following databases till 21 March 2018: MEDLINE, CINAHL, LILACS, EMBASE, the Cochrane Library, Internet Documents in Economics Access Service (IDEAS), Google Scholar, Web of Sciences, Social Services Abstracts, WHO Global Health Library, Global Health CABI and CAB Abstracts. We also searched grey literature in OpenGrey and websites of relevant organisations such as the World Bank, World Food Program and International Food Policy Research Institute. We also contacted authors of studies and members of our advisory board for any unpublished studies or grey literature reporting eligible studies. We checked reference lists of relevant studies and reviews. We also searched for trials registered with ClinicalTrials.gov and the WHO International Clinical Trials Registry Platform (http://www.who.int/trialsearch/).
Titles and abstracts were screened in duplicate by two reviewers. We pilot-tested the screening criteria at both title and abstract screening stage and full text stage. We used the PRISMA flow diagram to report eligibility of studies. We retrieved full text of all studies which pass this first level screening. The full text review were also done in duplicate by two reviewers, and agreement was reached by consensus. Disagreements were resolved by consultation with a third reviewer. No language or date limits were applied. The search strategy is attached as Appendix 1.
Description of methods used in primary research
RCTs of mass deworming include two-arm trials as well as factorial trials, with women allocated either individually or by cluster-randomisation.
Details of study coding categories
We extracted the study characteristics including details of the populations, setting, socio-demographic characteristics, interventions, comparators, outcomes and study design in duplicate. The characteristics extracted from the included studies are specified in Appendix 2.
Quality assessment and grading
Risk of bias was assessed at the study as well as the outcome level. At the study level, two independent reviewers performed quality appraisal for each study using the Cochrane risk of bias tool which assessed selection bias, performance bias, detection bias, attrition bias and reporting bias (Higgins, Altman & Sterne, 2011). Disagreements were resolved by discussion or consultation with a third reviewer. At the outcome level, we summarised the quality of evidence according to the outcomes as per the Grading of Recommendations Assessment, Development and Evaluation (GRADE) criteria (Walker et al., 2010). A grade of 'high', 'moderate', ‘low’ and ‘very low’ was used for grading the overall evidence indicating the strength of an effect on specific health outcome based on methodological flaws within the component studies, consistency of results across different studies, generalisability of research results to the wider patient base and how effective the treatments have shown to be (Balshem et al., 2011). The two reviewers discussed ratings and reached consensus. Disagreements were resolved by consulting a third reviewer. We developed a summary of findings table to show the effects for the primary outcomes of maternal anaemia and infection intensity; as well as the secondary outcomes of preterm birth, LBW and perinatal mortality since these outcomes assess long-term effects, particularly in terms of birth outcomes.
Statistical procedures and conventions
Trialists of the included trials provided IPD by electronic transfer where possible or other means as needed. The individual trial data were recoded as required and checked with respect to range, internal consistency, missing values, outliers, errors and consistency with published reports. Trial details such as randomisation methods and intervention details were cross-checked against published reports, trial protocols and data collection sheets. Inconsistencies or missing data were discussed with the individual trialists and attempts were made to resolve any problems by consensus. We did not exclude any study based on the way the outcomes were reported.
Data were prepared into a flat spread-sheet with the same fields for every study. We considered the missing values for each variable as missing at random (MAR). For this IPD, we restricted our analysis to conventional complete case analyses, that is, removing subjects with a missing value from the analyses, since the missing data were considered to be non-trivial. For future updates, we plan to use multiple imputation to impute the missing values for covariates at baseline (individual participant level variables) and outcome variables (primary and secondary outcomes). Imputation was planned to be done using Proc MI in SAS/STAT (SAS Institute Inc., Cary, NC). We plan to assess the robustness of the results by running a separate model excluding imputed data (i.e., complete case analysis). We plan to include studies with missing data on more than 50% of outcome or covariate data in the complete case analysis only for future updates.
Descriptive characteristics of each study were presented, with details on the participant characteristics, environment, worm species, prevalence, intensity of infection, geographic location, interventions, comparator, outcomes and risk of bias assessment. We accounted for clusters (such as villages, schools or households) as nested within each study. Following data items were collected:
Individual level: Infection intensity with Ascaris, Trichuris, hookworm and schistosomes (across four levels of none, light, moderate and heavy, using the WHO cutoffs for each helminth, available at: http://apps.who.int/iris/bitstream/10665/44671/1/9789241548267_eng.pdf) Anaemia status (using WHO cutoffs by age and altitude of non-anaemic, mild, moderate and severe, http://www.who.int/vmnis/indicators/haemoglobin.pdf) Undernutrition (BMI < 18.5 kg/m2) Socioeconomic status (as defined by trial authors): We assessed whether the measurement of socioeconomic status can be compared across study settings and time. Deworming drug used.
Environmental level: WASH practices (as defined by trial authors) Population level infection intensity (using WHO cut-offs for each worm-type, as above)
We calculated the standardised difference between the published data and the IPD received from authors for baseline characteristics and baseline outcome assessment. For endline (outcome measures), we replicated the effect measures reported in study publications and calculated the standardised difference between the IPD received and the study report (Austin, 2009).
The comparison of interest for the pairwise analysis included (but not restricted to) any deworming drug versus no deworming. We used a two-step process to meta-analysis. We conducted pairwise analyses for the comparison of interest by entering all IPD data into a multilevel model, with each study as one cluster. We expected considerable heterogeneity between studies for each outcome; therefore, we used a random effects model. Where IPD was not available for all trials, we used a two-part model with one part based on IPD data and the second part based on aggregate data from studies which did not provide IPD (Fisher, Copas, Tierney & Parmar, 2011; Riley & Steyerberg, 2010; Riley et al., 2008). We planned to conduct pair-wise comaprisons for one deworming drug versus other deworming drug or a combination of deworming drugs, however we could not perform such analysis due to limited data.
We accounted for clustering as above by nesting clusters within studies. We decided on a set of pre-defined covariates with advice from our advisory board and co-authors. We accounted for the pre-defined covariates of infection intensity, baseline anaemia, baseline nutritional status, socioeconomic status and maternal education in the model. We did not plan to conduct network meta-analysis based on our previous experience with limited number of studies in the domain (Salam et al., 2015).
Measures of treatment effects
We separately analysed the dichotomous and continuous outcomes. For dichotomous outcomes, we presented the results as summary risk ratios (RRs) with 95% confidence intervals (CI). We presented continuous outcome data as either a mean difference (MD), if outcomes have been measured on the same scale, or a standardised mean difference (SMD), if outcomes have been measured on different scales, with 95% CI. For each outcome, we reported the results for the evidence from study results pooled at the aggregate level (adjusted for covariates) and the evidence pooled using IPD (adjusted for covariates).
Assessment of clinical and methodological heterogeneity within treatment comparisons
Heterogeneity across trials in terms of subject characteristics, trial methodologies and treatment protocols was assessed using visual plots, tables and homogeneity statistics. We assessed heterogeneity using visual inspection of forest plots for pairwise analyses as well as statistical tests of heterogeneity (I 2). In addition to I 2, we also assessed between-study variance (variation across study findings beyond random sampling error) by the variance of the distribution of the true study effects, commonly denoted as τ 2.
Publication bias
We planned to generate a funnel plot for comparisons and outcomes with >10 studies. We planned to use Egger's test for asymmetry and visual inspection to assess the presence of publication bias and/or selective reporting. However, none of the comparisons or outcomes included >10 studies and hence we could not assess for publication bias.
Subgroup analyses
Where sufficient data were available, sub-group analyses was planned to be conducted to assess effects across both individual-level as well as environment-level characteristics. We compared the results of models with subgroup analyses by assessing the size of quantitative or qualitative differences in effects, the statistical significance of tests for interactions, assessing between-study variance and assessing the goodness of fit of the models using the likelihood ratio. Before conducting subgroup analyses, we assessed the distribution of each variable. If there were insufficient participants in some categories, the levels were combined. The following individual and environment level effect modifiers were planned to be assessed (data permitting):
Individual Level: Infection intensity with Ascaris, Trichuris, hookworm and schistosomes (across four levels of none, light, moderate and heavy, using the WHO cutoffs for each helminth, available at: http://apps.who.int/iris/bitstream/10665/44671/1/9789241548267_eng.pdf) Anaemia status (using WHO cutoffs by age and altitude of non-anaemic, mild, moderate and severe, http://www.who.int/vmnis/indicators/haemoglobin.pdf) Undernutrition (BMI < 18.5 kg/m2) Socioeconomic status (as defined by trial authors): We assessed whether the measurement of socioeconomic status can be compared across study settings and time.
Environmental Level: WASH practices (as defined by trial authors) Population level infection intensity (using WHO cut-offs for each worm-type, as above)
Sensitivity analyses
Where sufficient data were available, we planed to conduct sensitivity analyses to assess robustness of results when restricted to studies at low risk of bias for sequence generation, allocation concealment and blinding of participants. We planned to assess whether results were robust to excluding imputed data (i.e., complete case analysis).
Data management
Data were transferred to SAS as a common platform for all studies, using a common data dictionary. We checked IPD data for consistency immediately upon receiving datasets for outlier individuals (e.g. with duplicate participant IDs, unrealistic date ranges). We compared the IPD from authors with the aggregate data reported in the articles. Any missing or unusual data were flagged for discussion with the trial author or statistician. We asked for clarification from the authors to establish reasons for the errors, and correct them if possible. Any requests for authors were discussed when the data were provided, such as clarification of trial risk of bias, conduct or eligibility criteria. We also ran the same statistical analysis as the authors to check for consistency with the published paper (Stewart et al., 2015). We requested statements of ethics approval from each study and we did not include data from studies that did not receive ethics approval. We requested that all data be transferred without any identifiers.
Treatment of qualitative research
We did not plan to include qualitative research.
RESULTS
The results of this review are reported according to the PRISMA-IPD reporting guidelines (checklists in Additionals Table 1).
Search results
We searched all databases up to March, 2018. Figure 2 provides a search flow diagram. We identified a total of 23406 record through the search strategy provided in Appendix 1. A total of 31 papers (Atukorala, de Silva, Dechering, Dassenaeike & Perera, 1994; Villar et al., 1998; Abel, Rajaratnam, Kalaimani & Kirubakaran, 2000; Ács, Banhidy, Puho & Czeizel, 2005; Adam, Elwasila & Homeida, 2005; Christian, Khatry & West, 2004; De Silva, Sirisena, Gunasekera, Ismail & de Silva, 1999; Deepti & Nandini, 2015; Elliott, Mpairwe et al., 2005; Elliott, Namujju et al., 2005; Elliott et al., 2007; Gyorkos, Larocque, Casapia & Gotuzzo, 2006; Gyorkos, Gilbert et al., 2011; Larocque et al., 2006; Liabsuetrakul et al., 2009; Tehalia, 2011; Mpairwe et al., 2011; Millard et al., 2014; Nampijja et al., 2012; Ndibazza et al., 2010; Ndibazza et al., 2012; Ndyomugyenyi, Kabatereine, Olsen & Magnussen, 2008aa; Olveda et al., 2016; Torlesse & Hodges, 2000; Torlesse & Hodges, 2001; Tweyongyere et al., 2008; Tweyongyere et al., 2009; Tweyongyere et al., 2011; Tweyongyere et al., 2013; Urassa, Nystrom & Carlsted, 2011; Webb, Mawa et al., 2011; Webb, Kyosiimire-Lugemwa et al., 2012) based on 16 studies assessed mass deworming during pregnancy and were deemed eligible for the review. These 16 studies were assessed for IPD eligibility and seven studies with 8,515 participants were identified to be eligible for IPD. Major reasons for exclusion from IPD inlcuded: study design not being appropriate and; only abstracts were available with insufficient information and the trialists could not be contacted.

Search flow diagram
Out of the seven studies found eligible for IPD, three trials were subsequently included in the IPD since the authors of these three trials provided data for IPD (Elliott, Mpairwe et al., 2005; Olvedaet al., 2016; Urass et al., 2011). Table 1 details the study eligibility for IPD.
Eligibility for IPD
Abbreviation: IPD, individual participant data.
A total of seven studies including 8,515 pregnant women were eligible for IPD. All of these studies were RCTs. Studies were conducted in India, Philippines, Peru, Sierra Leone, Tanzania and Uganda between 2001 and 2016. The deworming drugs provided in these studies included albendazole, mebendazole, praziquantel, ivermectin or a combination of these. Majority of the studies provided mass deworming for STH only; while one study (Olveda et al., 2016) provided deworming for schistosomiasis alone; and one study (Elliott, Mpairwe et al., 2005) targeted both STH and schistosomiasis. The sample size ranged from 184 pregnant women to 3,080 pregnant women. The most common co-intervention was iron/folic acid supplementation while other interventions included food supplementation, anti-malarial drug administration and education. Maternal and birth outcomes were assessed in the third trimester and at the time of delivery in all the included studies. Table 2 describes the characteristics of studies eligible for IPD. Out of the seven studies, three trials were subsequently included in the IPD (Elliott, Mpairwe et al., 2005; Olveda et al., 2016; Urass et al., 2011) and further descritipion is provided in the following sections.
Characteristics of IPD eligible studies
Characteristics of IPD eligible studies
The quality of the studies was assessed using the Cochrane risk of bias assessment criteria. Overall, the included studies were judged to be of fairly good quality. For random sequence generation, five studies were judged to be at low risk of bias while two studies (Ndyomugyenyi et al., 2008aa; Urass et al., 2011) were rated as unclear since the method of sequence generation was not specified. Allocation concealment was judged to be adequately done in three studies (Larocque et al., 2005; Deepti & Nandini, 2015; Elliott, Mpairwe et al., 2005); three studies did not clearly specify the concealment of allocation and were judged to be at unclear risk (Torlesse & Hodges, 2000; Ndyomugyenyi et al., 2008aa; Urass et al., 2011) while one study did not adequately conceal the allocation and was rated as high risk for allocation concealment (Olveda et al., 2016). All the included studies either adequately blinded the participants, personnels and outcome assessors or we felt that lack of blinding would be unlikely to affect the results and hence all the studies were rated to be a low risk for blinding. Four studies were rated at low risk of attrition bias while two studies were rated to be at high risk of attrition bias (Torlesse & Hodges, 2000; Urass et al., 2011). All the studies were judged to be at low risk of bias for selective reporting since the outcomes specified in the study protocol or methodology section of the study were reprotred in the outcome section. We judged one study as unclear risk of bias for ‘other bias’ since in the (Elliott, Mpairwe et al., 2005) study, enrolment was stopped after 104 women due to new guidelines by the WHO which recommended inclusion of treatment of women with schistosomiasis. Figure 3a depicts the risk of bias for the studies included in the review while Figure 3b depicts the risk of bias for the studies subsequently included in the IPD.

(a) Risk of bias for the included trials. (b) Risk of bias for the trials included in IPD. IPD, individual participant data [Color figure can be viewed at wileyonlinelibrary.com]
Trial authors were contacted for all seven trials deemed eligible for the IPD. Out of the seven trials, we received data from three trials (Elliott, Mpairwe et al., 2005; Olveda et al., 2016; Urass et al., 2011); data from two trails were lost (Deepti & Nandini, 2015; Torlesse & Hodges, 2000; trialists were not able to retrieve the data); one trialist refused to share the data (Larocque et al., 2006) while one could not be contacted due to severe health conditions (Ndyomugyenyi et al., 2008aa). In terms of the number of participants; out of 8,515 potential IPD participants; data were captured for 5,957 participants. Figure 4 depicts the number of studies and participants eligibility for IPD.

Number of eligible studies and participants for IPD. IPD, individual participant data [Color figure can be viewed at wileyonlinelibrary.com]
Data preparation: missingness analysis
Tables 3 and 4 provides an overview of the missing values for the baseline and endline variables in the data sets from each of the trial.
Missing values for baseline variables
Missing values for baseline variables
Missing values for endline variables
Replication of the published study results was conducted for all three studies. The standardised differences between the published and replication results were all below 0.10 for all outcome measures and covariates. There were instances where the standardised difference could not be calculated because the published results did not report the outcome measure in question. Table 5 reports the standardised differences between the published and reproduced results for outcome measures.
Standardised differences between published and reproduced results for outcome measures by eligible studies
Standardised differences between published and reproduced results for outcome measures by eligible studies
Based on the availability of data, we could only analyse one comparison of interest (mass deworming with any drug versus no mass deworming). The planned analysis and final model was also modified accordingly. Table 6 provides a comparison of the original analysis plan and the actual analysis model.
Comparison of the original analysis plan and actual model employed
Comparison of the original analysis plan and actual model employed
This section provides the overall results for mass deworming compared to no mass deworming on the following outcomes: maternal anaemia; maternal infection intensity (T.Trichiura and hookworm); LBW and preterm birth. All of the seven trials deemed eligible for the IPD contributed data towards the aggregate estimate while data from three trials (Elliott, Mpairwe et al., 2005; Olveda et al., 2016; Urass et al., 2011) contributed to the IPD estimate. We report results for the evidence from study results pooled at the aggregate level (adjusted for covariates) and the evidence pooled using IPD (adjusted for covariates). However we advise caution in interpreting these findings due to small sample sizes.
Following this section, we describe effect modifier analyses for each planned effect modifier for each outcome of interest.
Maternal anaemia
The effect estimates from aggregate evidence were of similar size and direction as the IPD effect estimates. Three trials reported data on maternal anaemia. Mass deworming led to a 23% reduction in maternal anaemia (RR: 0.77, 95% CI: 0.73–0.81; three trials; 5,216 participants; moderate quality evidence). Table 7 reports the aggregate and IPD adjusted estimates.
Imapct of mass deworming on maternal anaemia
Imapct of mass deworming on maternal anaemia
Two trials reported T.Trichiura intensity showing no evidence of impact of mass deworming on any infection (RR: 0.69, 95% CI: 0.42–1.13; two trials; 2,867 participants; moderate quality evidence). We attempted to categorise the participants according to the intensity of infection (none, light, moderate and heavy); however there were too few participants in each category to draw meaningful conclusions. The effect estimates from aggregate evidence were of similar size and direction as the IPD effect estimates. Table 8 reports the aggregate and IPD adjusted estimates for maternal T.Trichiura intensity.
Mass deworming on T.Trichiura intensity (any infection)
Mass deworming on T.Trichiura intensity (any infection)
Two trials reported hookworm intensity. Overall there was no evidence of impact of mass deworming on any hookworm infection (RR: 0.52, 95% CI: 0.18, 1.47; two trials; 2,867 participants; moderate quality evidence). We attempted to categorise the participants according to the intensity of infection (none, light, moderate and heavy); however there were too few participants in each category to draw meaningful conclusions. The effect estimates from aggregate evidence were of similar size and direction as the IPD effect estimates. Table 9 reports the aggregate and IPD adjusted estimates for maternal hookworm intensity.
Mass deworming on hookworm intensity (any infection)
Mass deworming on hookworm intensity (any infection)
Two trials reported LBW suggesting no evidence of an impact of mass deworming on LBW (RR: 0.89, 95% CI: 0.67–1.18; two trials; 2,267 participants; moderate quality evidence). The effect estimates from aggregate evidence were of similar size and direction as the IPD effect estimates. Table 10 reports the aggregate and IPD adjusted estimates for LBW.
Mass deworming on LBW
Mass deworming on LBW
Two trials reported preterm birth suggesting no evidence of an overall impact (RR: 0.69, 95% CI: 0.47–1.03; two trials; 2,707 participants; moderate quality evidence). The effect estimates from aggregate evidence were of similar size and direction as the IPD effect estimates. Table 11 reports the aggregate and IPD adjusted estimates for preterm birth.
Mass deworming on preterm birth
Mass deworming on preterm birth
Based on the availability of the data, we could only assess for effect modification by baseline Trichiura infection, maternal anaemia at baseline and maternal BMI at baseline. The overall model suggested a marginally significant impact of deworming on maternal anaemia (RR: 0.77, 95% CI: 0.73–0.81) with no evidence of impact on Trichiura infection, hookworm infection, LBW and preterm birth. The test for interaction was not statistically significant across the levels of Trichiura infection at baseline, maternal anaemia at baseline or maternal BMI at baseline for any of the outcomes. There was no evidence of effect modification by baseline Trichiura infection, maternal anaemia at baseline and maternal BMI at baseline. Table 12 depicts the estimates for full model and effect modification.
Potential effect modification of mass deworming during pregnancy by baseline infection intensity, anaemia status and BMI
Potential effect modification of mass deworming during pregnancy by baseline infection intensity, anaemia status and BMI
Note: Bold font indicates statitiscally significant estimates.
These findings are summarised in the summary of findings table (Table 13). All the outcomes were rated to be of moderate quality evidence. The evidence was downgraded by one level due to the study limitations since estimates are based on a sleceted sample received to conduct IPD.
Summary of findings table
Abbreviations: CI, confidemce interval; LBW, low birthweight; RR, risk ratio; STH, soil transmitted helminths.
GRADE Working Group grades of evidence.
High quality: Further research is very unlikely to change our confidence in the estimate of effect.
Moderate quality: Further research is likely to have an important impact on our confidence in the estimate of effect and may change the estimate.
Low quality: Further research is very likely to have an important impact on our confidence in the estimate of effect and is likely to change the estimate.
Very low quality: We are very uncertain about the estimate.
Downgraded for study limitations - obtained only a selected sample of IPD.
Summary of main results
This IPD meta-analysis is based on the data from three trials with 5,957 participants. The effect estimates from aggregate evidence were of similar size and direction as the IPD effect estimates. Findings from this IPD suggest reduction in anaemia among pregnant women with mass deworming. There was no evidence of effect on any of the other outcomes including Trichiura infection, hookworm infection or any of the pregnancy outcomes including LBW and preterm birth. Findings of no impact of mass deworming on infection intensity could be attributable to the fact that majority of the study population in the included studies were either not infected or lightly infected which could have diluted the impact. Based on the availability of the data, we could only assess for effect modification by baseline Trichiura infection, maternal anaemia at baseline and maternal BMI at baseline. There was no evidence of effect modification by Trichiura intensity at baseline, maternal anaemia at baseline and maternal BMI at baseline; however we advise caution in interpreting these findings due to limited number of participants included in the analysis.
Overall completeness and applicability of evidence
Findings from this IPD analysis is based on 70% of the existing data deemed eligible for IPD (5957 participiants of 8515 participants). The studies included in this review were conducted among pregnant women in LMIC settings. One of the three trials included in the IPD analysis provided daily iron folate supplements (36 mg iron; 5 mg folate) along with the deworming drugs.
We conducted an extensive search of electronic databases, with advice from the Campbell Collaboration International Development Group information scientist. We screened 23406 articles and updated this search to March 2018. We report the systematic review according to the reporting guidelines for IPD meta-analysis (PRISMA-IPD). We published and followed an a priori protocol (Salam et al). Our systematic review and IPD analysis was approved by the Research Ethics Boards at SickKids. We developed a data sharing agreement that was signed by all studies that contributed data. Study authors were invited to join the Investigator's Collaborative, participate in meetings and contribute to the final report. Our process and conduct of the IPD was driven by consultation with our expert Advisory board which included statistical, parasitology and nutrition expertise.
Quality of the evidence
The trials included in the IPD were judged to be of fairly good quality. All of the included studies were judged to be at low risk of bias for blinding of participants, personnel and outcome assessor; and selective reportong. One of the included studies was judged to be at high risk of bias for allocation concealment while two studies were at high risk for attrition bias. The overall outcome quality was judged to ‘moderate’ based on the GRADE criteria. The outcome quality was downgraded due to study limitations since the estimates are based on selected sample eligible for IPD.
Limitations and potential biases in the review process
Despite of receiving majority of the existing data (70%) to conduct IPD, there were a few limitations. One limitation of this review is that we did not receive data from all eligible studies. Another limitation is that we were unable to assess effect modification by pre-idnetified effect modifiers. The trials did not capture many of the variables of interest that restricted our analysis. Very few trials reported outcomes according to the baseline level of infection intensities and hence those conclusions could not be drawn. In terms of the infection intensities, the population studied were either not infected or lightly infected and hence it was difficult to categorise the sample according to the intensity of infection and have meaningful estimates. Trials did not report baseline data on the individual and environmental level effect modifiers and hence it was difficult to assess the effect modification. Variables like socio-economic status were least studied and where reported, had different definitions and hence could not be accounted for. None of the included studies assessed any co-interventions including WASH practices and hence the impact of co-interventions could not be assessed. We could not assess for publication bias given the small number of included studies; however, considering the small universe of studies in the domain, the issues related to publication and small study sizes cannot be ignored.
Agreements and disagreements with other studies or reviews
The most recent Cochrane meta-analysis (Salam et al., 2015) on deworming for STH during pregnancy concluded that there was insufficient evidence to recommend deworming for STH. This review also highlighted the need for future well-designed, large scale RCTs to establish the benefit. These findings were based on four trials including 4265 participants. This review has some differences compared to our review. The inclusion criteria for this Cochrane review was limited to deworming for STH alone while our IPD meta-analysis also included trials with deworming for schistosomiasis. The Cochrane review reported no impact of mass deworming for STH on maternal anaemia while findings from our review suggests reduction in maternal anaemia associated with mass deworming,
Implications for policy
This systematic review and IPD suggest that mass deworming reduces maternal anaemia with moderate quality evidence. The policy implications are that, even in high-prevalence areas, deworming alone is insufficient to achieve improvements in all maternal and newborn health outcomes. These findings reinforce that it is essential to focus on sustainable development to address the other factors such as poor sanitation, food insecurity and malnutrition. Mass deworming should be bundled as part of these packages to improve range of maternal and newborn health outcomes.
Implications for research
There is a need to evaluate mass deworming for STH and schistosomiasis during pregnancy in large scale programmatic settings. Future impact evaluations should attempt to measure various individual and environmental factors that could potentially effect the impact of mass deworming. Future program evaluations should also assess the long term impact of mass deworming on birth and infant health outcomes along with the maternal health outcomes. There is an urgent need for open data from all research studies. The quality of evidence is rated as moderate for our findings. Further research on maternal baseline worm intensities and birth outcomes could change our findings.
Footnotes
ACKNOWLEDGEMENT
We would like to acknowledge Sajid Muhammad and Pravheen Thurairajah for their assistance with the data cleaning and coding. We would also like to acknowledge the trial authors for sharing their data sets for the IPD.
PLANS FOR UPDATING THE REVIEW
This review will be updated if funds become available.
SOURCES OF SUPPORT
This review is funded by the Bill and Melinda Gates Foundation (Funding reference number: OPP1140742).
DECLARATIONS OF INTEREST
Michelle Gaffey, Robert Black, Deidre Hollingsworth, Sue Horton, Rehana Salam, and Simon Cousens have no conflict of interest, financial or otherwise that may influence judgments made in this review.
Celia Holland is a co-author and principal investigator on a randomised trial of deworming in children: Kirwan et al 2009 (Kirwan, P., Asaolu, S. O., Molloy, S. F., Abiona, T. C., Jackson, A. L. & Holland, C. V. (2009). Patterns of soil-transmitted helminth infection and impact of four-monthly albendazole treatments in preschool children from semi-urban communities in Nigeria: a double-blind placebo-controlled randomised trial. BMC infectious diseases, 9(1), 20.)
Vivian Welch and Zulfi Bhutta are authors of the Campbell systematic review and network meta-analysis of mass deworming for children (Welch, Ghogomu et al. 2016).
Vivian Welch is editor-in-chief of the Campbell Collaboration.
AUTHORS CONTRIBUTION
Rehana A Salam and Michelle Gaffey collated the data for IPD; Simon Cousens supervised the statistical analysis; Paul Arora, Vivian Welch, Robert Black, Celia Holland, Deirdre Hollingsworth, Sue Horton Sanjay Wijesekera, Philippa Middleton, Maria Makrides and Zulfiqar A Bhutta provided overall feedback at each stage.
DIFFERENCE BETWEEN PROTOCOL AND REVIEW
We could not conduct the following analyses as planned due to limited number of included studies We could not conduct planned pair-wise comaprisons for one deworming drug versus other deworming drug or a combination of deworming drugs. We could not assess for publication bias as planned due to < 10 studies included. We could not conduct the planned subgroup analysis and effect modification.
