Indoor air quality of low and middle income urban households in Durban, South Africa.

Environ Res

Discipline of Occupational and Environmental Health, School of Nursing and Public Health, University of KwaZulu-Natal, 321 George Campbell Building, Howard College Campus, Durban 4041, South Africa.

Published: July 2017

Introduction: Elevated levels of indoor air pollutants may cause cardiopulmonary disease such as lower respiratory infection, chronic obstructive lung disease and lung cancer, but the association with tuberculosis (TB) is unclear. So far the risk estimates of TB infection or/and disease due to indoor air pollution (IAP) exposure are based on self-reported exposures rather than direct measurements of IAP, and these exposures have not been validated.

Objective: The aim of this paper was to characterize and develop predictive models for concentrations of three air pollutants (PM, NO and SO) in homes of children participating in a childhood TB study.

Methods: Children younger than 15 years living within the eThekwini Municipality in South Africa were recruited for a childhood TB case control study. The homes of these children (n=246) were assessed using a walkthrough checklist, and in 114 of them monitoring of three indoor pollutants was also performed (sampling period: 24h for PM, and 2-3 weeks for NO and SO). Linear regression models were used to predict PM and NO concentrations from household characteristics, and these models were validated using leave out one cross validation (LOOCV). SO concentrations were not modeled as concentrations were very low.

Results: Mean indoor concentrations of PM (n=105) NO (n=82) and SO (n=82) were 64μg/m (range 6.6-241); 19μg/m (range 4.5-55) and 0.6μg/m (range 0.005-3.4) respectively with the distributions for all three pollutants being skewed to the right. Spearman correlations showed weak positive correlations between the three pollutants. The largest contributors to the PM predictive model were type of housing structure (formal or informal), number of smokers in the household, and type of primary fuel used in the household. The NO predictive model was influenced mostly by the primary fuel type and by distance from the major roadway. The coefficients of determination (R) for the models were 0.41 for PM and 0.31 for NO. Spearman correlations were significant between measured vs. predicted PM and NO with coefficients of 0.66 and 0.55 respectively.

Conclusion: Indoor PM levels were relatively high in these households. Both PM and NO can be modeled with a reasonable validity and these predictive models can decrease the necessary number of direct measurements that are expensive and time consuming.

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Source
http://dx.doi.org/10.1016/j.envres.2017.03.008DOI Listing

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