Figures
Abstract
Background
Trachoma is the commonest infectious cause of blindness worldwide. Efforts are being made to eliminate trachoma as a public health problem globally. However, as prevalence decreases, it becomes more challenging to precisely predict prevalence. We demonstrate how model-based geostatistics (MBG) can be used as a reliable, efficient, and widely applicable tool to assess the elimination status of trachoma.
Methods
We analysed trachoma surveillance data from Brazil, Malawi, and Niger. We developed geostatistical Binomial models to predict trachomatous inflammation—follicular (TF) and trachomatous trichiasis (TT) prevalence. We proposed a general framework to incorporate age and gender in the geostatistical models, whilst accounting for residual spatial and non-spatial variation in prevalence through the use of random effects. We also used predictive probabilities generated by the geostatistical models to quantify the likelihood of having achieved the elimination target in each evaluation unit (EU).
Results
TF and TT prevalence varied considerably by country, with Brazil showing the lowest prevalence and Niger the highest. Brazil and Malawi are highly likely to have met the elimination criteria for TF in each EU, but, for some EUs, there was high uncertainty in relation to the elimination of TT according to the model alone. In Niger, the predicted prevalence varied significantly across EUs, with the probability of having achieved the elimination target ranging from values close to 0% to 100%, for both TF and TT.
Conclusions
We demonstrated the wide applicability of MBG for trachoma programmes, using data from different epidemiological settings. Unlike the standard trachoma prevalence survey approach, MBG provides a more statistically rigorous way of quantifying uncertainty around the achievement of elimination prevalence targets, through the use of spatial correlation. In addition to the analysis of existing survey data, MBG also provides an approach to identify areas in which more sampling effort is needed to improve EU classification. We advocate MBG as the new standard method for analysing trachoma survey outputs.
Author summary
Trachoma is the most common infectious cause of blindness worldwide. Achieving elimination in resource-limited settings requires pragmatic strategies, including determining the likelihood that the elimination prevalence targets have been reached. Model-based geostatistics (MBG) is a branch of spatial statistics that can underpin highly efficient methods for designing surveys and analysing surveillance data for NTD programmes. Here, we illustrate the application of the MBG framework to analyse trachoma surveillance data from Brazil, Malawi, and Niger. Using the elimination criteria set by WHO, we predict the likelihood of elimination thresholds for trachomatous inflammation—follicular (TF) and trachomatous trichiasis (TT) having been achieved in each evaluation unit in each of the three countries. MBG is a statistically rigorous approach to quantify the likelihood around the exceedance of elimination prevalence thresholds. By providing a way to identify areas where there is more uncertainty about the achievement of elimination, MBG could be used to select areas in which more intensive sampling efforts should be undertaken.
Citation: Sasanami M, Amoah B, Diori AN, Amza A, Souley ASY, Bakhtiari A, et al. (2023) Using model-based geostatistics for assessing the elimination of trachoma. PLoS Negl Trop Dis 17(7): e0011476. https://doi.org/10.1371/journal.pntd.0011476
Editor: Alberto Novaes Ramos Jr, Federal University of Ceará, Fortaleza, Brazil, BRAZIL
Received: March 1, 2023; Accepted: June 26, 2023; Published: July 28, 2023
Copyright: © 2023 Sasanami et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: The data used for the analyses in this paper are owned by the governments of the countries in which the original surveys were conducted. Permission to use the data for our analyses was obtained via formal agreements between those governments and the involved universities and organisations; all data were de-identified before use. Researchers are welcome to request access to the same de-identified datasets by contacting the International Trachoma Initiative at: support@tropicaldata.org.
Funding: AWS is a staff member of the World Health Organization. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: AB and SB are employed by the International Trachoma Initiative, which receives an operating budget and research funding from Pfizer Inc., the manufacturers of Zithromax (azithromycin). EMHE receives salary support from the International Trachoma Initiative.
Introduction
Trachoma, one of twenty neglected tropical diseases (NTDs), remains the leading infectious cause of blindness globally [1,2]. It is caused by the bacterium Chlamydia trachomatis, which is transmitted from person to person by ocular and nasal secretions of infected people, during direct contact between individuals, or indirectly via flies or fomites [3–5]. Trachoma is prevalent in the most deprived and marginalised communities where crowded living conditions are common and access to clean water and sanitation is limited [2,6–9]. In endemic areas, trachomatous inflammation—follicular (TF), a sign of active trachoma, is common among children aged 1–9 years [2,10]. After years of repeated infections, some individuals develop prominent conjunctival scarring and have their upper eyelids turn inward so that the eyelashes rub against the globe. This is referred to as trachomatous trichiasis (TT), which can require surgery to prevent visual impairment and blindness [2]. TT and loss of vision are generally more common in women than in men [11,12], since the former are more likely to care for young children and therefore be exposed to more episodes of infection [2]. Although blindness caused by trachoma is generally considered irreversible, it is possible to prevent it, primarily using the surgery, antibiotics, facial cleanliness, and environmental improvement (SAFE) strategy promoted by the World Health Organization (WHO) [13,14].
In 1996, WHO launched the WHO Alliance for the Global Elimination of Trachoma by 2020 (GET2020) to eliminate trachoma as a public health problem [15]. Elimination is defined as: (i) a prevalence of TT unknown to the health system < 0.002 (0.2%) in adults aged ≥ 15 years, in each formerly endemic evaluation unit (EU) and (ii) a prevalence of TF < 0.05 (5%) in children aged 1–9 years, in each formerly endemic EU; plus (iii) the presence of a system to identify and manage incident cases of TT, which are expected to arise for many years after the prevalence thresholds (i) and (ii) are met. An EU for assessment of elimination is defined as the administrative unit for health care management, which typically contains a population of between 100,000 and 250,000 persons [16]. In the standard approach, the age- or age- and gender-specific prevalences of TF among children aged 1–9 years or TT among adults aged ≥ 15 years, respectively, are calculated. They are then standardised using the proportion of population expected to have that age or age-gender, according to the most recent census data available [17]. At the time of acceptance of this paper in June 2023, 17 countries had been validated by WHO as having eliminated trachoma as a public health problem [18].
The decision on whether a country has achieved the elimination criteria has to be informed by accurate and precise estimates of disease prevalence. This can be challenging in settings with very low prevalence and spatially sparse data, which is often the case in trachoma surveys. A possible solution to this is to sample a larger proportion of the population, however, this is usually infeasible due to resource constraints. The 4th Global Scientific Meeting on Trachoma recommended that national programmes could combine data from multiple adjacent EUs [19], which would allow improvement in estimates of disease prevalence at one location by (for example) using information from nearby EUs. Model-based geostatistics (MBG) [20] is an established set of spatial statistical methods that has been increasingly used in low-resource settings to inform disease control programmes. In a recent study of TT mapping in Ethiopia, MBG methods were used to assess the elimination status of EUs; it was shown that this approach yielded substantially more precise estimates of TT prevalence compared to the standard trachoma prevalence survey approach [21].
The objective of this paper is to demonstrate the general applicability of MBG methods to assess the elimination of trachoma in different settings. To this end, we predict TF and TT prevalence using trachoma data collected from Brazil, Malawi, and Niger. These countries were selected as they differ in their trachoma elimination status, as described in detail in the Methods section below. Through these three case studies, we demonstrate how statistically rigorous MBG methods are used for borrowing the strength of information across space and making the best possible use of spatially sparse trachoma survey data. We also provide a framework to guide the inclusion of gender and age effects in MBG for trachoma.
Methods
Country settings
Brazil: From the 18th to the early 20th century, trachoma was spread through migrant populations in Brazil’s Northeast and the São Francisco Valley. The Federal Government led control campaigns from 1923 to 1998 [22], and in the 1970s, trachoma was considered eradicated in São Paulo. This belief (in eradication) became generalised across the entire country, leading to decreased engagement in surveillance and control activities. To better understand the contemporary burden of trachoma among children, school surveys were implemented in municipalities with Human Development Index (HDI) below the national mean in the early 2000s [23–25]. A nationwide study [26] found that 11 (41%) of 27 surveyed states had a prevalence of TF ≥ 5% (although participants included those aged ≥ 10 years). These results led to strengthening of national surveillance and control activities for trachoma [26,27], including antibiotic treatment of individuals with active trachoma and their contacts, identified through active case finding and contact tracing. This contributed to a marked decline in the TF prevalence between 2008 and 2016, as evidenced by the Brazil Information System for Notifiable Diseases (SINAN) [27]. A recent study showed that the prevalences of TF and TT were below the target for elimination in eight of nine surveyed non-indigenous EUs in 2018–19 [27]. In this most recent survey series, as is traditional, prevalence was estimated using a standard statistical approach that adjusts for age for TF, and age and gender for TT [17]. The prevalence among indigenous communities has not been recently estimated; this is currently under investigation.
Malawi: Since the 1980s, Malawi has recognised trachoma as an endemic disease [28,29]. A population-based survey conducted in two districts in Central and Southern Malawi in 2008 showed a prevalence of TF ≥ 10% (a threshold prevalence defined by WHO for determining the duration of annual mass drug administration [MDA]) and TT ≥ 0.2%, indicating trachoma was a public health problem [30]. Based on these findings, the Ministry of Health launched its first national-level trachoma control programme to implement the SAFE strategy, whilst stressing the need to estimate prevalence in other regions. Through surveys conducted between 2013 and 2015 with the support of the Global Trachoma Mapping Project (GTMP), trachoma mapping was officially completed in all suspected endemic areas, showing that some EUs in Central and Southern Malawi exceeded the TF and TT elimination thresholds [31,32]. Subsequently, the country intensified its efforts to eliminate trachoma and in 2022 was validated by WHO as having eliminated the disease, based on TF and TT prevalences [33].
Niger: After identifying almost all regions as being endemic for trachoma, Niger started SAFE implementation in 1999 and expanded it nationally in 2009 [34]. In order to determine eligibility for district- or sub-district-wide SAFE implementation, 31 district-level trachoma prevalence surveys were conducted from 2009 to 2012. The prevalence of TT in ≥ 15-year-olds ranged from 0.1–5.4% and the prevalence of TF in 1–9-year-olds ranged from 0.1–42.4%, suggesting the need for continued SAFE interventions in 16 districts, primarily in eastern Niger [34]. As of June 2022, 41 out of 72 health districts were identified as having TT prevalence ≥ 0.2%, and a combined population of more than three million people required the A, F and E interventions to reduce EU-level TF prevalence to < 5% [35].
Data
We obtained the data from trachoma baseline, impact and pre-validation surveillance surveys [36,37] conducted in Brazil, Malawi, and Niger. All surveys were supported by Tropical Data and used a standardised two-stage cluster sampling methodology as defined by the GTMP [17,36,38]. Briefly, the first stage involves selection of 20–30 clusters (villages) using a probability-proportional-to-size sampling method, followed by the second-stage selection of approximately 30 households within each cluster, using compact segment, systematic, or random sampling. Consenting residents had both eyes examined for TF and TT using WHO’s simplified grading system for trachoma [39]. A case of TT was defined as an individual aged ≥ 15 years who had at least one eyelash touching the eyeball or showed evidence of recent epilation of in-turned eyelashes. Cases were excluded if the individuals (i) had TT post-operatively, (ii) had refused surgery, or (iii) were listed for surgery but had not yet received an operation.
Specifically, we used the data from nine Brazil EUs surveyed in 2018–19, 18 Malawi EUs surveyed in 2017–19, and 85 Niger EUs surveyed in 2017–19. The Brazil data were exclusively from baseline (i.e. pre-intervention) surveys. In Malawi and Niger, depending on the EU, impact and/or surveillance (i.e. post-intervention) surveys were available. When both impact and surveillance surveys were available in the same administrative unit, we just used the data from the most recent survey. As a result of this, only surveillance surveys were analysed in the case of Malawi. In the analysis for Brazil, we focused on the six EUs of north-eastern Brazil, namely Nordeste Paraense, Leste Maranhense, Noroeste Cearense, Sertão Pernambucano, Sertão Alagoano, and Vale São do Francisco da Bahia. We did not include the data from the north part of Brazil, from Vale do Jurua, Sudoeste Amazonense, and Norte de Roraima, because in those EUs, only 13 TF cases were detected in 2,318 examined children, and only one TT case was detected in 5,891 examined individuals aged ≥ 15 years, making the use of any statistical model infeasible.
Geostatistical model
We developed geostatistical Binomial models for prevalence of TF and TT that account for age (for TF) or age and gender (for TT), as fixed effects, and for unexplained Binomial extra variation through the use of random effects. We express the general form of the models for TF and TT as follows.
Based on existing scientific evidence and also guided by a preliminary exploratory analysis, we have summarised our approach for the introduction of age and gender effects in Table 1. In the model for TF, we defined the trend of age effect using a linear spline with a knot at the age of 3 years, since it is expected that prevalence should increase until around age 2–4 years followed by a decline [2,10]. This expectation was supported by our data on TF for Malawi and Niger, with the highest prevalence at age 3 years. In Brazil, prevalence showed a steady increase with increasing age, hence, we introduced age as a logit linear effect. The reason for preferring linear splines over other smoothing techniques is because of their greater interpretability for the effects of the covariates on trachoma prevalence [40]. Also, in the models for TF, we did not introduce any gender effect, since there is no strong scientific evidence to support a consistent difference in exposure to C. trachomatis between male and female children [2].
In the model for TT, we controlled for gender [11,12,41] regardless of statistical significance level, and introduced age as logit linear effect [2,10]. However, we did not introduce the gender effect in Brazil because it was not possible to distinguish between prevalence in males and females due to the small number of cases detected. Because differences in age trends could be observed between males and females for TT due to differences in mean exposure to C. trachomatis [41–43] and possibly sex-related biological phenomena [44], we decided to include an age-gender interaction in the model if this was statistically significant at the 95% confidence level. The final form of the model for each sign and country is described in Table A in S1 Text.
All data analysed in this study showed evidence of residual spatial correlation for both TF and TT. To address this, the geostatistical models fitted to the data included two types of random effects. More specifically, we included a spatial random effect, modelled as a Gaussian process, and unstructured random effects, modelled as Gaussian noise. The former accounts for between-cluster variation whilst the latter accounts for within-cluster variation.
We predicted local TF and TT prevalence by first laying grid squares over the EUs and computing prevalence for each age or age-gender class within each grid. We defined the areas shown in Fig A in S1 Text as EUs for prevalence prediction in this study, and the spatial resolution was determined based on the estimated scale of the spatial correlation for each country (see S1 Text). To allow for comparison with the standard approach [17], we then standardised prevalence for age bands of one-year for TF, and gender-specific five-year age bands for TT, using EU-specific population census data in Brazil (2010 census) [45] and national census data in Malawi (2018 census) and Niger (2012 census) [46,47]. To account for spatial heterogeneities in population density in generating the EU-wide standardised average prevalence for TF and TT, we weighted the predictions for each pixel using the population density data obtained from WorldPop [48].
Finally, we obtained 10,000 predictive samples for the EU-wide standardised average prevalence, for both TF and TT, and used the 10,000 samples to compute: the point prediction of the EU-wide standardised average prevalence, using the mean of the predictive samples; the 95% confidence-level prediction intervals; and the probability of elimination having been achieved, computed as the proportion of predictive prevalence samples that fell below the elimination threshold. We used R for all analyses, including the package “PrevMap” [49] to perform the geostatistical analysis. Technical details of the approach are provided in S1 Text.
Results
Table 2 shows crude (unadjusted) TF and TT prevalence in Brazil, Malawi, and Niger. For both TF and TT, Brazil had the lowest crude prevalence whilst Niger had the highest. The crude TF prevalence by country, including data from all available EUs in that country, ranged from 0.44% to 3.66%. For TT, the prevalence was higher among females than males in Malawi and Niger, although this gender difference was not observed in Brazil, where only 11 cases were detected amongst 12,603 people aged ≥ 15 years examined.
According to the models, point predictions for both TF and TT prevalence in Brazil were below the elimination thresholds (Fig 1). In Malawi, the predicted TF prevalences were below the threshold, whereas six areas had a TT prevalence above the threshold. In Niger, the North-western regions had lower predicted TF prevalence and the South-eastern had higher, ranging from 0.5% to 15.7%. A similar trend was observed for TT prevalences.
The boundaries and names shown and the designations used on this map are based on Global Administrative Areas (GADM) [50] and do not imply the expression of any opinion whatsoever on the part of the authors, or the institutions with which they are affiliated, concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.
We found that in Brazil, it is highly likely that TF prevalence met the target across all EUs (Fig 2). The probability of TT being below the elimination threshold (<0.2%) was more than 90% in three EUs out of six. For Sertão Pernambucano, Vale do São Francisco da Bahia, and Noroeste Cearense, the probability was 85%, 78%, and 70%, respectively. Similarly for Malawi, models indicated that the elimination criterion for TF had been met with greater than 95% likelihood. However, results are more uncertain for TT in one EU in particular, namely Dedza East, where the likelihood of achievement of elimination was 28%. In Niger, the probability for TF and TT spanned the full range of values, from ~0% to 100%. For TF, 65 of 107 EUs had likely met the elimination target with a probability of more than 95%, although 20 EUs likely had not, with a probability of having met the elimination target of less than 50%. For TT, 8 EUs had a more than 95% likelihood, whilst 38 EUs had less than 50%.
The boundaries and names shown and the designations used on this map are based on Global Administrative Areas (GADM) [50] and do not imply the expression of any opinion whatsoever on the part of the authors, or the institutions with which they are affiliated, concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries.
Discussion
We have demonstrated the use of MBG methods for assessing trachoma elimination through three case studies, involving data from Brazil, Malawi, and Niger. Our approach can be adapted to different contexts to reflect data availability and age-gender trends, which can vary substantially across countries. We also showed that MBG methods can be applied to different epidemiological settings, ranging from very low prevalence settings such as Brazil and Malawi to relatively high prevalence settings such as Niger. One crucial aspect in which our MBG framework differs from the standard approach for the analysis of trachoma prevalence survey data is that it provides a probability statement on the exceedance or not of the elimination threshold. Quantification of uncertainty is essential to better inform the decision-making process and identify areas where the data do not provide enough information on achievement of elimination. This statistical aspect is ignored by the standard approach. For this reason, we argue that the model-based geostatistical approach presented in this paper is an important methodological improvement that answers more directly the problem of achievement of elimination for TF and TT in a given EU.
As noted at the 4th Global Scientific Meeting on Trachoma, an efficient survey analysis strategy is vital for trachoma programmes [19]. As prevalence decreases, it becomes more challenging to precisely predict the prevalence without increasing the sample size. MBG provides one of the most efficient solutions to this, by allowing unsampled locations to borrow information from neighbouring sampled locations [51–53]. We show here that MBG can be effectively used in different epidemiological settings, both with very low trachoma prevalence, such as Brazil and Malawi, and relatively high prevalence, such as Niger. Future extensions of the proposed MBG framework will aim to incorporate spatially referenced covariate effects to account for well-established factors associated with trachoma, such as temperature, elevation, and precipitation [54]. However, whilst it is generally good practice to use covariates to aid spatial predictions of prevalence, it can be problematic in the context of low prevalence. This is because, as prevalence declines, the association between covariates and disease becomes more difficult to discern empirically and we would be wary of applying poorly estimated regression relationships to predict prevalence at unsampled locations. For example, in our case studies, the low levels of prevalence observed in Brazil and Malawi would likely make the use of covariates infeasible.
In the case of Brazil, the results obtained from our MBG approach are largely comparable to those generated using the standard approach (which have already been made publicly available [27]). Indeed, we observed that the 95% prediction intervals of the EU-wide standardised average prevalence from our MBG models overlap with those from the standard approach (see S1 Text), with the only exceptions being the prevalence estimates previously reported as 0% [27] and from Vale do São Francisco da Bahia, where there was only one TF case amongst 614 examined. Using the standard approach, we would conclude that prevalence was below the elimination threshold for both TF and TT in almost all EUs. However, our MBG approach, which also considers the uncertainty in the EU-wide prevalence predictions, indicated that although all EUs achieved TF prevalence < 5% with nearly 100% confidence, there was some uncertainty that TT prevalence was < 0.2%. The highest level of uncertainty was in Noroeste Cearense, where we found a likelihood of TT elimination of 70%. More data might be collected from this EU to establish without ambiguity whether the TT elimination prevalence threshold has been reached.
Malawi’s results from our analysis were mostly in accordance with WHO’s validation of it having achieved the elimination goal (for which the data from the most recent surveys were also used) [33]. The model indicated that the elimination criterion for TF was met with greater than 95% likelihood, as shown in Fig 2. For TT prevalence, however, the point predictions were above the elimination threshold of 0.2% for six EUs analysed, and it was shown that there was more uncertainty in the achievement of elimination particularly in Dedza East. The MBG analytical approach provides more tangible quantification of uncertainty in prevalence predictions, facilitating more informed discourse about exactly how much uncertainty policymakers are willing to tolerate, whilst also identifying the areas where sustained monitoring and resource allocation should be targeted even after elimination has been attained.
In all three countries, we found evidence of residual spatial correlation in the data which justified the use of MBG. However, in other settings, it is possible that the data will not show strong evidence of this, making the estimation of MBG models more difficult. In that scenario, a model-based approach for the estimation of EU-wide prevalence might still be achieved by simplifying the structure of our statistical models. More specifically, the spatial Gaussian process component which is introduced in all our models could be removed and extra-Binomial variation could be accounted for using unstructured random effects only. When using this simpler model, the generation of EU-wide standardised prevalence estimates and probabilities of elimination are obtained following the approach illustrated in this paper with only minimal technical adjustments.
When generating the EU-wide average prevalence using the illustrated model-based geostatistical approach, each pixel is weighted according to the WorldPop population density estimates. As a result of this, we should point out that the WorldPop data are based on model predictions and therefore could be uncertain if the input population data are not recent and/or not accurate due to considerable subnational variations in migration, fertility, and mortality [55].
As shown here, the MBG process must be guided by both contextual knowledge and empirical data exploration. These were especially important when deciding how to incorporate age and gender. For example, in our analysis for Brazil, TF prevalence showed a steady increase with increasing age, which differed from the pattern observed in other settings [30,41,56]. Hence, unlike for Malawi and Niger, we decided to include age as a logit linear effect which we justify as follows. First, the data were not informative enough to allow us to estimate a more complex relationship between prevalence and age. Second, individuals diagnosed as having TF might have conjunctivitis precipitated by a stimulus other than C. trachomatis infection. Scientific understanding of the diseases that cause a similar presentation to TF is currently incomplete [57–59], and disentangling them from trachoma requires further research. Finally, for the TT analysis in Brazil, we did not include gender effects. We based this decision on the fact that gender differences were so small that we could not precisely estimate them from the data. We also point out that the assumption of a logit linear trend in age for TT prevalence should be carefully assessed, especially in older ages. For example, in settings where TT surgery is offered to a population and awareness of, acceptance of and access to the service is high, age effects might be obscured.
MBG has been used for the analysis of various infectious diseases [60–67]. Recently, it was proposed as an efficient tool to determine sampling and analysis strategies for NTD elimination surveys [53]. Soil-transmitted helminths (STH) are one of several NTDs for which MBG may become widely used [52,68–71]; the same framework can be applied to trachoma and, more broadly, to other NTDs. We advocate MBG as the new standard method to help NTD control programmes efficiently achieve their targets worldwide.
Acknowledgments
We are grateful to all our colleagues who contributed to generating the survey data on which these secondary analyses are based, and to the residents of trachoma-endemic communities examined as part of those surveys, who remain our enduring partners in trachoma elimination.
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