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Assessment of Soil Transmitted Helminth Infection (STHI) in School Children, Risk Factors, Interactions and Environmental Control in El Salvador.Malavade, Sharad Suryakant 16 September 2015 (has links)
Background:
Soil transmitted helminth infections (STHI) are important Neglected Tropical Diseases (NTD). The three main STHI are infections with Ascaris lumbricoides, Trichuris trichiura and hookworms. STHI have a significant effect on the growth and development of children. A national survey for STHI in El Salvador by Pan American Health Organization and Ministry of Health in 2012 in school children aged 8years to 10 years. The survey collected data on age, gender, behavioral habits, and source of drinking water, type of toilet facility used and ecological zone of residence.
A) We did an analyses of the data with an aim to determine the prevalence of STHI in El Salvador, assess the risk factors and risk interactions.
B) We also aimed to determine the efficacy of urea as a potential additive for inactivation of Ascaris suum in solar toilets.
Methods:
A) Data from 1310 subjects was analysed for determination of prevalence of STHI in El Salvador. Risk factor assessment was done by chi-square test, unadjusted logistic regression and fully adjusted logistic regression. Risk factor interactions was tested on multiplicative and additive scale.
B) Urea was tested for efficacy in inactivation of Ascaris suum ova in 20 solar toilets. Under conditions of controlled pH and moisture, concentration of gas ammonia, peak temperature were measured along with duration of treatment with urea to determine viability of Ascaris suum samples placed in the solar toilets.
Results:
I) The prevalence of Ascaris lumbricoides in 8-10 year old school children is 2.75%, Trichuris trichiura is 4.1% and hookworm is 1.83%.
A) For Ascaris lumbricoides infection: Significant risk in individuals from volcanic chains and central depression compared to those from the mountains. Spring or well water when used as source of drinking water was associated with higher risk of infection when compared with piped water. Higher infection was also associated with open air defecation compared to use of septic tank or flush toilet. Use of sandals or no footwear was associated with a higher risk of infection when compared to use of closed footwear at all times.
B) For Trichuris infection: Coastal plains were associated with a higher risk of infection compared to the mountains while rural status was protective against infection. Spring or well water when used as source of drinking water was associated with higher risk of infection when compared with piped water. Use of sandals or no footwear was associated with a higher risk of infection when compared to use of closed footwear at all times.
C) For hookworm infection: Risk of infection was higher in individuals from urban regions. Spring or well water when used as source of drinking water was associated with higher risk of infection when compared with piped water. Use of sandals or no footwear was associated with a higher risk of infection when compared to use of closed footwear at all times. Poor handwashing was shown to be protective against infection with hookworm.
Significant risk factor interactions were identified for infection with each of the three soil transmitted helminths.
II) Urea as an additive at 1%w/w to feces tested in solar toilets showed an inactivation rate of nearly half the Ascaris suum ova samples. Fifty percent or higher inactivation rates were associated with ammonia gas concentrations of 109.5 ppm or higher and duration of treatment of 72 hours or higher.
Conclusions: Prevalence of STHI in 8-10 year old school children for 2012 in El Salvador is low. Significant risk factors for STHI in El Salvador are eco-epidemiologic zone, source of drinking water, type of sanitation, use of shoes behavior and urban status of place of residence. Use of urea for inactivation of soil transmitted helminth ova in feces is a possible intervention for environmental control of STHI.
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Inactivation of <i>Ascaris suum</i> by Ammonia in Feces Simulating the Physical-Chemical Parameters of the Solar Toilet Under Laboratory ConditionsCruz Espinoza, Ligia Maria 10 November 2010 (has links)
Access to sustainable sanitation systems is a determining factor in human health and economic development. However, more than a third of the world’s population lives without access to improved sanitation facilities. To meet the sanitation United Nations Millennium Development target, "halve, by 2015, the proportion of people without sustainable access to safe drinking water and basic sanitation", a wide range of non conventional sanitation technologies have been implemented in developing countries, including waterless systems. These systems function by diverting urine away from feces and collecting, storing, and dehydrating the fecal material in watertight dehydration vaults. From a public health perspective, adequate inactivation of fecal pathogens in a sanitation system is essential before any use or disposal of fecal material. In rural areas of El Salvador, the solar toilet is capable of inactivating fecal pathogens and reducing the prevalence of parasitic infections in its users when compared to other waterless systems. Nevertheless, not all solar toilets are able to inactivate completely Ascaris spp. ova after the recommended storage period. Un-ionized ammonia (NH3) has the potential to inactivate pathogens in solutions and sludge, including Ascaris spp. ova. This study hypothesized that adding ammonia to the solar toilet will improve the technology since pathogen inactivation with ammonia could be potentiated by the alkaline medium and high temperatures achieved inside the toilet vaults.
To evaluate this approach, a series of experiments in solution and biosolid were performed in a laboratory environment using physical and chemical parameters similar to those achieved by the solar toilet. Eggs of the swine Ascaris species, Ascaris suum, were used as model in all experiments. In ammonia solution, the parasite ova were stored for a period of three days and; in biosolid, the parasite ova were stored for two months. Urea was used as the source of ammonia in biosolid. In addition to the experiments with ammonia, normal viability and morphological changes within the parasite ova during incubation in vitro at 28 C° were investigated and described to complement current literature published.
Results from the experiments in ammonia solution indicated that addition of ammonia (1% and 2%) could improve the system since the critical parameters that significantly reduced A. suum ova viability to zero in three days could be achieved by the solar toilet: temperature of 35°C or higher and pH value of 9.3. Results from the experiments in biosolid further showed that inactivation of A. suum ova was faster in samples exposed to urea and to temperatures higher than 28°C. All samples exposed to urea achieved 100% inactivation after 14 days (28°C), 3 days (35°C) and 24 hours (40°C and 45°C). Survival analysis of the data showed that there was a significant difference (p value <.0001) between the inactivation achieved in the samples exposed to urea (1% and 2%) and the samples not exposed to urea. A logistic regression analysis estimated the effect of Urea (Treatment, OR: 25.9), Temperature (OR: 1.8), and Storage (OR: 1.17) on inactivation.
Results from the experiment with A. suum ova in normal incubation solution showed that the ova went through clearly identified morphological changes at different speed of development. Two new additional stages of development were identified (Pre-larva 1 and Pre-larva 2) and no significant statistical difference was observed among the viability reported early in incubation and the one reported after three weeks of in vitro incubation, indicating that early stages of development may be use as an alternative to reduce the time to report viability.
The results of this study suggest that inactivation of Ascaris spp ova by ammonia is possible in fecal material stored in the solar toilet or any other dry toilet, if the following physical and chemical conditions are met: a closed vault with a minimum temperature of 28°C; an initial pH of 8.3, minimum moisture of 27.5%, and addition of 1% urea to the biosolid. At 28°C longer storage time would be required for 100% inactivation while at higher temperatures less time of storage would be necessary. A community intervention is recommended to include field conditions and human behavior as other predictors for Ascaris spp. inactivation by ammonia.
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