Helminths are positively associated with atopy and wheeze in Ugandan fishing communities: results from a cross-sectional survey

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Study Justification:
The study aimed to investigate the association between helminth infections and allergy-related conditions in heavily helminth-exposed fishing villages in Uganda. The study was conducted to test the hypothesis that helminth infections would be inversely associated with allergy-related conditions.
Highlights:
– The study surveyed 2,316 individuals in fishing villages on Lake Victoria, Uganda.
– Prevalence of reported wheeze was 2% in under-fives and 5% in participants ≥5 years.
– 19% of participants had a positive skin prick test (SPT) for allergies.
– Helminth infections, including S. mansoni, N. americanus, S. stercoralis, T. trichiura, M. perstans, and A. lumbricoides, were prevalent in the population.
– Positive associations were found between certain helminth infections and allergy-related outcomes, such as Dermatophagoides-specific IgE, SPT, cockroach-specific IgE, and wheeze in participants ≥5 years.
– No inverse associations were observed between helminth infections and allergy-related outcomes.
Recommendations:
Based on the study findings, the following recommendations can be made:
1. Further research is needed to understand the mechanisms underlying the positive associations between certain helminth infections and allergy-related outcomes.
2. Public health interventions should focus on preventing and treating helminth infections in heavily helminth-exposed communities.
3. Education and awareness programs should be implemented to promote hygiene practices and reduce the risk of helminth infections.
4. Healthcare providers should be trained to recognize and manage allergy-related conditions in helminth-exposed populations.
Key Role Players:
To address the recommendations, the following key role players are needed:
1. Researchers and scientists to conduct further studies on the association between helminth infections and allergy-related conditions.
2. Public health officials and policymakers to develop and implement interventions targeting helminth infections.
3. Healthcare providers to diagnose and treat helminth infections and manage allergy-related conditions.
4. Community leaders and educators to promote hygiene practices and raise awareness about helminth infections and allergy-related conditions.
Cost Items for Planning Recommendations:
While the actual cost may vary, the following cost items should be considered in planning the recommendations:
1. Research funding for further studies on helminth infections and allergy-related conditions.
2. Budget for public health interventions, including helminth treatment programs and hygiene education campaigns.
3. Healthcare resources and personnel training for diagnosing and managing helminth infections and allergy-related conditions.
4. Community outreach and education programs to raise awareness and promote behavior change.
5. Monitoring and evaluation costs to assess the effectiveness of interventions and measure outcomes.

The strength of evidence for this abstract is 7 out of 10.
The evidence in the abstract is relatively strong, but there are some areas for improvement. The study design is a cross-sectional survey, which limits the ability to establish causality. Additionally, the sample size is not mentioned, which makes it difficult to assess the statistical power of the study. To improve the evidence, future studies could consider using a longitudinal design to establish temporal relationships and increase the sample size to improve statistical power.

Background: Parasitic helminths are potent immunomodulators and chronic infections may protect against allergy-related disease and atopy. We conducted a cross-sectional survey to test the hypothesis that in heavily helminth-exposed fishing villages on Lake Victoria, Uganda, helminth infections would be inversely associated with allergy-related conditions. Methods: A household survey was conducted as baseline to an anthelminthic intervention trial. Outcomes were reported wheeze in last year, atopy assessed both by skin prick test (SPT) and by the measurement of allergen-specific IgE to dust mites and cockroach in plasma. Helminth infections were ascertained by stool, urine and haemoparasitology. Associations were examined using multivariable regression. Results: Two thousand three hundred and sixteen individuals were surveyed. Prevalence of reported wheeze was 2% in under-fives and 5% in participants ≥5 years; 19% had a positive SPT; median Dermatophagoides-specific IgE and cockroach-specific IgE were 1440 and 220 ng/ml, respectively. S. mansoni, N. americanus, S. stercoralis, T. trichiura, M. perstans and A. lumbricoides prevalence was estimated as 51%, 22%, 12%, 10%, 2% and 1%, respectively. S. mansoni was positively associated with Dermatophagoides-specific IgE [adjusted geometric mean ratio (aGMR) (95% confidence interval) 1.64 (1.23, 2.18)]; T. trichiura with SPT [adjusted odds ratio (aOR) 2.08 (1.38, 3.15)]; M. perstans with cockroach-specific IgE [aGMR 2.37 (1.39, 4.06)], A. lumbricoides with wheeze in participants ≥5 years [aOR 6.36 (1.10, 36.63)] and with Dermatophagoides-specific IgE [aGMR 2.34 (1.11, 4.95)]. No inverse associations were observed. Conclusions: Contrary to our hypothesis, we found little evidence of an inverse relationship between helminths and allergy-related outcomes, but strong evidence that individuals with certain helminths were more prone to atopy in this setting.

LaVIISWA is being conducted in 26 fishing villages on the Lake Victoria islands of Koome subcounty, Mukono district, Uganda, a remote setting accessible in 2–3 h from Entebbe by powered canoe. Full details of the trial design are described elsewhere 29. The baseline household survey was conducted between October 2012 and July 2013, across all trial villages, immediately preceding intervention roll‐out. All households in participating villages were eligible for inclusion in the survey. Available household listings were checked and updated by the research team, and simple random samples of 45 households were selected from each village. In selected households, all members were eligible for inclusion in the survey. Questionnaires were completed regarding household features and individual social‐demographic characteristics. Information regarding asthma, eczema and allergy symptoms was obtained using questions from the International Study on Allergy and Asthma in Children (ISAAC) questionnaire, with supplementary questions from the UK diagnostic criteria for atopic eczema 30, 31. A general history and examination, including height, weight and hepatosplenomegaly, was performed. All individuals were examined for visible flexural dermatitis: for this, all team members were trained in the standardized approach described in 32. SPTs were performed on participants aged ≥1 year, using standard methods, with three allergens [Dermatophagoides mix, Blomia tropicalis and German cockroach (Blatella germanica)] and positive and negative controls (ALK‐Abelló; supplied by Laboratory Specialities (Pty) Ltd., Randburg, South Africa). Each participant was asked for one stool sample; mid‐stream urine samples were requested from all participants in the 15 villages surveyed from February 2013 onwards. Blood samples of 14 ml were obtained from individuals ≥13 years, 10 ml from children 5–12 years and 6 ml from children 1–4 years. Individuals were offered HIV counselling and testing in collaboration with local health service providers. Ethical approval was granted by the Research and Ethics Committee of the Uganda Virus Research Institute, the Uganda National Council for Science and Technology, and the London School of Hygiene and Tropical Medicine. Individual written informed consent (for adults ≥18 years and emancipated minors, and for children by a parent or guardian) and assent (for children 8–17 years) was sought for survey participation. Two slides from each stool sample were examined (by different technicians) using the Kato‐Katz method 33. The remaining sample was suspended in ethanol and stored at −80°C to allow further investigation for Necator americanus and Strongyloides stercoralis, and, among a subset of 200 participants, for Ancylostoma duodenale, using real‐time polymerase chain reaction (RT‐PCR) 34. Quality control for PCR assays was conducted at St Elisabeth’s Hospital, Tilburg, NL. The Uganda results were comparable for N. americanus and A. duodenale, but had a lower detection rate for S. stercoralis. The presence of circulating cathodic antigen (CCA) of S. mansoni in urine was assessed (Rapid Medical Diagnostics, Pretoria, South Africa). Infection intensity based on Kato‐Katz results was classified using WHO‐recommended cut‐offs 35. For PCR results, there are no standard cut‐offs for categorizing infection intensity; however, based on results from Verweij et al. 34, individuals with C t > 30 would have parasite loads difficult to detect by microscope. Mansonella perstans infection was determined by a modified Knott’s method 36; malaria was determined by thick blood film. IgE specific to Dermatophagoides and cockroach allergens was measured by ELISA 29. The lower detection limit for our in‐house ELISA was 15.6 ng/ml. We used 20‐fold diluted plasma samples in our assay; hence, the lower detection limit in undiluted plasma was calculated as 312 ng/ml. This was used as a cut‐off to create binary variables for detectable vs undetectable responses for each allergen. This was a cross‐sectional analysis of survey data. Outcomes were reported wheeze in the last 12 months for children <5 years and for participants ≥5 years; visible flexural dermatitis; atopy defined as positive SPT response to any allergen for participants ≥1 year; atopy assessed as concentration of asIgE and analysed both as a continuous outcome and as detectable/nondetectable using the cut‐off of 312 ng/ml. Exposures for the analysis were helminth infections. The following variables were considered as potential confounders: individual socio‐demographic characteristics (age, sex, birth order, number of siblings, area of birth, area resided in for first 5 years, preschool attendance; occupation, maternal tribe, paternal tribe); behavioural and clinical characteristics (hand‐washing behaviour, BCG scar, maternal or paternal allergy/asthma/eczema, immunization history, breastfeeding, exposure to anthelminthic treatment in utero, anthelminthic treatment in last 12 months, artemisinin combination treatment for malaria in last 12 months, malaria infection, HIV infection); and household characteristics (crowding, animal ownership, asset score, indoor cooking, toilet access, drinking water source, washing water source, malaria control measures). Assuming an average of 2.8 people per household, we expected that sampling 45 households per village would yield at least 3250 participants. For common exposures (prevalence ≥20%), assuming a design effect of 1.5 and outcome prevalence of 10%, the study would have over 80% power to detect risk ratios ≥1.5. All analyses employed the ‘svy’ survey commands in Stata to allow for clustering of respondents within villages using linearized standard errors 37 and for variable village sizes using weights. Village‐level weights were calculated based on the numbers of included and total households in each village. For binary outcomes, univariable and multivariable logistic regressions were used to obtain crude and adjusted odds ratios (OR) and 95% confidence intervals (CI). P‐values were calculated using Wald tests. Adjustment was made for any potential confounder for which there was evidence of crude association with the outcome or which was considered to have a possible role, a priori. Raw asIgE responses were skewed. Therefore, we used simple and multiple linear regressions to examine the association between helminth infections and log10 levels of asIgE, and back transformed results to obtain geometric mean ratios (GMRs) and 95% CIs. For all outcomes, the role of S. mansoni infection intensity was assessed using the test for trend. The population attributable fraction (PAF) for reported wheeze due to atopy was estimated as p’(OR−1)/OR with p’ the prevalence of a positive SPT response among individuals with reported wheeze and OR the odds ratio for the wheeze–SPT association. We prespecified that we would examine whether helminth infections modified the associations between the atopy and the wheeze outcomes, by fitting interaction terms in multivariable logistic regression models. We also undertook a series of additional exploratory interaction analyses between helminth infections for each outcome, in an attempt to understand the primary association findings. Finally, as most previous studies have been performed in children, we conducted an exploratory investigation into whether associations between allergy‐related outcomes and between helminths and allergy‐related outcomes differed by age group (<16 vs ≥16 years).

Based on the provided information, it is difficult to determine specific innovations for improving access to maternal health. The text primarily focuses on a study conducted in fishing villages in Uganda and the associations between helminth infections and allergy-related conditions. To provide recommendations for improving access to maternal health, it would be helpful to have more information about the specific challenges and context related to maternal health in the area.
AI Innovations Description
Based on the provided description, the recommendation to improve access to maternal health would be to implement a comprehensive maternal health program in the fishing villages on Lake Victoria, Uganda. This program should include the following components:

1. Antenatal care: Ensure that all pregnant women in the fishing villages have access to regular antenatal check-ups, including prenatal screenings, vaccinations, and nutritional support.

2. Skilled birth attendance: Train and deploy skilled birth attendants to provide safe and hygienic deliveries in the fishing villages. This will help reduce maternal and neonatal mortality rates.

3. Postnatal care: Establish postnatal care services to monitor the health of both mothers and newborns after delivery. This should include breastfeeding support, immunizations, and postpartum check-ups.

4. Family planning services: Provide access to family planning methods and counseling to empower women to make informed decisions about their reproductive health and spacing of pregnancies.

5. Health education and awareness: Conduct community-based health education programs to raise awareness about the importance of maternal health, safe delivery practices, and the prevention of common complications during pregnancy and childbirth.

6. Infrastructure and transportation: Improve the accessibility of the fishing villages by investing in infrastructure development, such as roads and transportation systems, to ensure that pregnant women can easily access healthcare facilities.

7. Collaboration with local health service providers: Collaborate with local health service providers to strengthen the healthcare system in the fishing villages and ensure the sustainability of the maternal health program.

By implementing these recommendations, access to maternal health services can be improved in the fishing villages, leading to better health outcomes for mothers and newborns.
AI Innovations Methodology
Based on the provided information, here are some potential recommendations to improve access to maternal health:

1. Mobile Clinics: Implement mobile clinics that can travel to remote areas, such as the fishing villages on Lake Victoria, to provide maternal health services. These clinics can offer prenatal care, antenatal check-ups, and delivery services, ensuring that pregnant women have access to essential healthcare closer to their homes.

2. Telemedicine: Utilize telemedicine technology to connect pregnant women in remote areas with healthcare professionals. This would allow them to receive virtual consultations, advice, and guidance throughout their pregnancy, reducing the need for physical travel to healthcare facilities.

3. Community Health Workers: Train and deploy community health workers in fishing villages to provide basic maternal health services. These workers can conduct health education sessions, assist with prenatal care, and provide referrals to higher-level healthcare facilities when necessary.

4. Transportation Support: Improve transportation infrastructure and provide support for pregnant women to access healthcare facilities. This can include subsidizing transportation costs, establishing transportation networks, or providing transportation vouchers to pregnant women in need.

To simulate the impact of these recommendations on improving access to maternal health, a methodology could include the following steps:

1. Define the baseline: Collect data on the current state of maternal health access in the fishing villages, including the number of pregnant women, distance to healthcare facilities, and utilization rates of existing services.

2. Model the interventions: Use a simulation model to estimate the potential impact of each recommendation on improving access to maternal health. This can involve estimating the number of pregnant women reached, the reduction in travel time, and the increase in utilization rates.

3. Input data: Gather data on the implementation of each recommendation, such as the number of mobile clinics deployed, the coverage of telemedicine services, the number of trained community health workers, and the level of transportation support provided.

4. Run simulations: Use the collected data and simulation model to run multiple scenarios, simulating the impact of each recommendation on improving access to maternal health. This can include estimating the number of additional pregnant women receiving care, the reduction in maternal mortality rates, and the improvement in health outcomes.

5. Analyze results: Analyze the simulation results to determine the effectiveness of each recommendation in improving access to maternal health. Compare the outcomes of different scenarios to identify the most impactful interventions.

6. Refine and iterate: Based on the analysis, refine the recommendations and simulation model if necessary. Iterate the simulation process to further optimize the interventions and improve access to maternal health.

By following this methodology, policymakers and healthcare providers can make informed decisions on which recommendations to prioritize and implement to improve access to maternal health in the fishing villages.

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