Table 1.
No. | Country | Name/year of study | Setting | Study design | Study period | Primary/secondary data | Age in months | Exposure | Data collected using | Sample size | Outcome parameter | Main result |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | India | Broor et al. (2001) | Peri-urban | Case-control | March 1995–February 1997 | Primary | < 60 | Solid fuel use | Questionnaire | 512 | Single disease episode | Cooking with any other type of fuel other than LPG (OR 2.5, 1.51–4.16) |
2 | India | Sharma et al. (1998) | Peri-urban | Case-control | November 1994–February 1995 | Primary | < 12 | Fuel used for cooking | Questionnaire | 642 | Multiple disease episode | Pneumonia was the most common illness in both fuel groups used at home for both wood and kerosene |
3 | India | Bassani et al. (2010) | Urban/rural | Case-control | February 1998 | Secondary | < 48 | Solid fuel use | Survey data | 616,391 | Mortality and single disease episode | Generally, children (0–4 years) with pneumonia had a higher reported solid fuel use compared to children without pneumonia (boys: PR 1.5, 1–2.4; girls: PR 1.9, 1.1–3.3) |
4 | Nepal | Dhimal et al. (2010) | Peri-urban | Cross-sectional | October 2008–January 2009 | Primary and secondary | < 60 | Fuel used for cooking | Questionnaire | 545,777 | Single disease episode | The solid biomass fuel was the primary source of energy for cooking which attributed to about 50% of the burden of pneumonia in children |
5 | Botswana | Kelly et al. (2015) | Urban/peri-urban | Cohort study | April 2012–April 2014 | Primary | < 24 | Wood smoke exposure | Questionnaire | 284 | Single disease episode and mortality | The risk of failure to respond to treatment at 48 h was increased in households that used wood as a cooking fuel (RR 1.44, 95% CI 1.09–1.92, P = 0.01). This effect was observed in undernourished children (P = 0.02) |
6 | Gambia | Dionisio et al. (2012) | Urban/peri-urban | Case-control | July 2007–January 2011 | Primary | < 60 | Exposure to CO | CO measurement questionnaire | 1181 | Single disease episode | There was an increased risk of pneumonia (OR 4.2, 3.1–5.7) in the rainy season compared to the dry season. Households where firewood or charcoal was purchased exposed children 2.0 (1.2–3.2) or 3.8 (2.1–7.1) times more to indoor air pollution compared to households that collected firewood |
7 | Gambia | Howie et al. (2016) | Urban/peri-urban | Case-control | June 2007-September 2010 | Primary | < 60 | Exposure to CO | CO measurement questionnaire | 1581 | Single disease episode | No association was found between CO exposure and childhood pneumonia. However, bed sharing with someone with a cough and severe pneumonia (OR 5.1, 3.2–8.2) and non-severe pneumonia (OR 7.3, 4.1–13.1). Undernutrition was associated with childhood pneumonia (OR 8.7, 4.2–17.8) |
8 | Indonesia | Shibata et al. (2014) | Urban | Cross-sectional/case-control | June 2011–June 2012 | Primary | < 60 | Measured PM2.5 and PM10 | PM2.5 measurement questionnaire | 461 | Single disease episode | Hourly sampling showed significant differences in PM2.5 and PM10 concentration between households in which children with pneumonia lived compared with controls |
9 | Bangladesh | Ram et al. (2014) | Urban | Case-control | March 2009–March 2010 | Primary | < 60 | Exposure to PM2.5 | PM2.5 measurement questionnaire | 994 | Single disease episode | PM2.5 was not significantly associated with pneumonia. However, crowding, aluminium roofing in living space, households with lower socioeconomic status and being a boy were associated with pneumonia |
10 | India | Mahalanabis et al. (2002) | Urban/peri-urban | Case-control | December 1997–November 1998 | Primary | < 35 | Risk factors | Questionnaire | 262 | Single disease episode | Solid fuel use with OR 3.97, 2–7.88, compared to not using any solid fuel for cooking |
11 | Nepal | Karki et al. (2014) | Peri-urban and rural | Case-control | June 2012–May 2013 | Primary | < 60 | Risk factors | Questionnaire | 200 | Single disease episode | Using solid fuel with location within living area (OR 3.76, 1.20–11.82) |
12 | Tanzania | PrayGod et al. (2016) | Urban/peri-urban | Case-control | May 2013–March 2014 | Primary | < 60 | Behaviour | Questionnaire | 117 | Single disease episode | Cooking indoors increased the risk of developing severe pneumonia (OR 5.5, 1.4–22.1) compared to cooking outdoors |
13 | Malawi | Mortimer et al. (2017) | Rural | Randomised control trial | December 2013–February 2016 | Primary | < 60 | Biomass smoke | Questionnaire and exposure measurement | 10,543 | Mortality and single disease | Cleaner burning biomass-fuelled cookstoves did not reduce the risk of pneumonia in young children under 5 in Malawi |
14 | Guatemala | Smith et al. (2011) | Rural | Randomised control trial | October 2002–December 2004 | Primary | < 18 | Household air pollution | Questionnaire and exposure measurement | 534 | Mortality and single disease episode | Reduction of wood smoke exposure with chimney stoves did not significantly reduce pneumonia in children under 5 |