help button home button
AJRCCM
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS

This Article
Right arrow Full Text (PDF)
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in PubMed
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Jaakkola, M. S
Right arrow Articles by Jaakkola, J. J. K
Right arrow Search for Related Content
PubMed
Right arrow PubMed Citation
Right arrow Articles by Jaakkola, M. S
Right arrow Articles by Jaakkola, J. J. K
American Journal of Respiratory and Critical Care Medicine Vol 174. pp. 851-852, (2006)
© 2006 American Thoracic Society
doi: 10.1164/rccm.2604004


Editorials

Biomass Fuels and Health

The Gap between Global Relevance and Research Activity

Maritta S Jaakkola, M.D., D.Sc and Jouni J. K Jaakkola, M.D., D.Sc., Ph.D

Institute of Occupational and Environmental Medicine University of Birmingham, Edgbaston, Birmingham, United Kingdom

The greatest burden on health related to biomass fuels affects the world's poorest and most vulnerable populations. Approximately half of the world's population, and up to 90% of households in rural areas of developing countries, still depend on unprocessed biomass fuels, mainly wood, dung, and crop residues, for cooking and heating (1, 2). These are burned indoors in open fires and stoves that often are not vented. Combustion is incomplete and leads to high indoor concentrations of substances harmful to health, such as respirable particles (PM), carbon monoxide, nitrogen oxides, polycyclic organic hydrocarbons, and other toxic compounds (3). In developing countries, women are traditionally responsible for cooking, and consequently the exposures are highest for them and for their infants and young children, who are often carried on their mother's back. Typically, exposure to high levels of pollutants lasts for 3 to 7 hours daily over many years (2). In global perspective, the magnitude of the health consequences of indoor air pollution, biomass fuels being the major source, is comparable to that of tobacco use, exceeded only by malnutrition, poor water/sanitation, and unsafe sex (4).

What do we know about the health effects of biomass fuels? The known or suggested adverse effects include common respiratory diseases, along with low birth weight and increased infant mortality (2, 3), and even DNA damage (5). Considering the extent of biomass fuel exposure, it is surprising how little research there is to date on its health consequences. At present, the strongest evidence exists for a relation between biomass fuel exposure and acute respiratory infections in children, with effect estimates for incidence and mortality ranging from two- to threefold (6). Other major respiratory effects that have been linked to biomass fuels more or less consistently include chronic obstructive pulmonary disease, asthma, nasopharyngeal and laryngeal cancer, and susceptibility to pulmonary tuberculosis (2, 3).

In this issue of the Journal (pp. 901–905), a study of more than 800 women from a rural community in Mexico investigated the relations between biomass fuel cooking and respiratory symptoms and lung function (7). The study demonstrates that it is feasible to carry out studies applying high-quality research methods in the often-difficult conditions of developing countries. This is important for getting reliable effect estimates and also for being able to assess adequately the benefits from any interventions aiming at solving these problems.

Earlier studies have shown an increase in respiratory symptoms and lung function impairment related to biomass fuel burning in children and in adults (2, 813), but there have been some methodologic issues, such as compromised validity of exposure assessment and limited control for confounding. To address these problems, the Mexican study (7) measured particle concentrations while cooking was in progress with the usual fuel, thus also capturing peak concentrations. In addition, it estimated a cumulative exposure index combining reported daily exposure in hours with years of exposure (hour-years) to assess lifetime biomass fuel exposure. The results showed high PM10 peak concentrations of the order of 2,600 µg/m3 during biomass combustion and large lifetime exposures with the mean cumulative index of 114 hour-years. High PM levels of 500 to 2,500 µg/m3 have been reported also from other developing countries, including Guatemala (14), India (15), and Nepal (13). Peak PM10 over 2,600 µg/m3 among those using biomass fuels was related to small, but significant reductions in FEV1 (–81 ml), FVC (–122 ml), and FEV1% predicted (–4.7) (7). The effects were smaller compared with previous hospital-based case-control studies (911), but still comparable to the estimates from environmental tobacco smoke exposure in adults (16). Taking into account the extent of biomass fuel exposure in rural communities, the effect is likely to have significant impact on the health of women in developing countries. Questionnaire-reported current exposure and cumulative hour-years were significantly related to occurrence of cough and phlegm production, with a small increase also detected for wheezing in the past. The study also adjusted for potential confounding factors, such as age, passive smoking and socioeconomic status. Income served as a proxy for the latter and is a relevant confounder, since people's possibilities for using cleaner fuels are strongly related to their income.

A limitation of the study is its small reference group of women with exposure to gas only, which reduces the power of this otherwise rather large study. Even more important is the fact that practically all women had previous exposure to biomass fuels, most of them in their childhood. This means that current biomass fuel exposure could not be contrasted to "never exposure," but instead to "no recent exposure," so the effect estimates are underestimated. The strongest effects on lung function were detected in relation to high current concentrations of PM10, so how much of the effect is acute and perhaps reversible and how much of it is long-term reduction that cannot be recovered remains somewhat unclear. Distinguishing these two types of effects is important from a preventive point of view and, in the future, development of better assessment methods for long-term exposures and longitudinal assessment of the change in lung function over time are needed. In many developing countries, smoking by men indoors is also common, and the interactions between tobacco smoke and biomass fuel exposures may add to the health problems, but this has not been studied.

From the global preventive perspective, the key question is the strong link between poverty and use of biomass fuels. Sustainable development calls for interventions that replace biomass fuels with more processed and cleaner fuels, that improve stoves, ventilation, and housing conditions in general, and that educate women about behavioral possibilities to reduce the exposure to themselves and their children. Sustainable development also requires that these interventions should be affordable and easy to implement. Research on biomass fuels and evidence-based interventions should be a high global priority, since reducing indoor biomass fuel exposures locally in developing countries would contribute to simultaneous reduction of harmful outdoor pollutants (3). Indeed, giving more emphasis to such interventions could be a cost-effective way to reduce globally the harmful pollutants leading to the greenhouse phenomenon.

Acknowledgments

The authors thank Professor Margaret R. Becklake for her valuable comments on the editorial.

FOOTNOTES

Conflict of Interest Statement: Neither author has a financial relationship with a commercial entity that has an interest in the subject of this manuscript.

REFERENCES

  1. World Resources Institute, UNEP, UNDP, World Bank. 1998–99 world resources: a guide to global environment. Oxford, UK: Oxford University Press; 1998.
  2. Bruce N, Perez-Padilla R, Albalak R. Indoor air pollution in developing countries: a major environmental and public health challenge. Bull World Health Organ 2000;78:1078–1092.[Medline]
  3. Smith KR. Indoor air pollution in developing countries: recommendations for research. Indoor Air 2002;12:198–207.[CrossRef][Medline]
  4. Murray CJL, Lopez A. Global mortality, disability, and the contribution of risk factors: Global Burden of Disease Study. Lancet 1997;349:1436–1442.[CrossRef][Medline]
  5. Pandey AK, Bajpayee M, Parmar D, Rastogi SK, Mathur N, Seth PK, Dhawan A. DNA damage in lymphocytes of rural Indian women exposed to biomass fuel smoke as assessed by the Comet assay. Environ Mol Mutagen 2005;45:435–441.[CrossRef][Medline]
  6. Smith KR, Samet JM, Romieu I, Bruce N. Indoor air pollution in developing countries and acute lower respiratory infections in children. Thorax 2000;55:518–532.[Abstract/Free Full Text]
  7. Regalado J, Pérez-Padilla R, Sansores R, Ramirez JIP, Brauer M, Paré P, Vedal S. The effect of biomass burning on respiratory symptoms and lung function in rural Mexican women. Am J Respir Crit Care Med 2006;174:901–905.[Abstract/Free Full Text]
  8. Behera D, Jindal SK, Malhotra HS. Ventilatory function in non-smoking rural Indian women using different cooking fuels. Respiration (Herrlisheim) 1994;61:89–92.
  9. Dossing M, Khan J, al-Rabiah F. Risk factors for chronic obstructive lung disease in Saudi Arabia. Respir Med 1994;88:519–522.[Medline]
  10. Dennis RJ, Maldonado D, Norman S, Baena E, Martinez G. Wood smoke exposure and risk for obstructive airways disease among women. Chest 1996;109:115–119.[Abstract/Free Full Text]
  11. Perez-Padilla R, Regalado J, Vedal S, Pare P, Chapela R, Sansores R, Selman M. Exposure to biomass smoke and chronic airway disease in Mexican women: a case-control study. Am J Respir Crit Care Med 1996;154:701–706.[Abstract]
  12. Rinne ST, Rodas EJ, Bender BS, Rinne ML, Simpson JM, Galer-Unti R, Glickman LT. Relationship of pulmonary function among women and children to indoor air pollution from biomass use in rural Ecuador. Respir Med (In press)
  13. Shrestha IL, Shrestha SL. Indoor air pollution from biomass fuels and respiratory health of the exposed population in Nepalese households. Int J Occup Environ Health 2005;11:150–160.[Medline]
  14. Albalak R, Bruce N, McCracken JP, Smith KR, De Gallardo T. Indoor respirable particulate matter concentrations from an open fire, improved cookstove, and LPG/open fire combination in a rural Guatemalan community. Environ Sci Technol 2001;35:2650–2655.[Medline]
  15. Balakrishnan K, Parikh J, Sankar S, Padmavathi R, Srividya K, Venugopal V, Prasad S, Pandey VL. Daily average exposures to respirable particulate matter from combustion of biomass fuels in rural households in Southern India. Environ Health Perspect 2002;110:1069–1075.[Medline]
  16. Jaakkola MS, Jaakkola JJK. Effects of environmental tobacco smoke on the respiratory health of adults. Scand J Work Environ Health 2002;28:52–70.




This Article
Right arrow Full Text (PDF)
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Similar articles in this journal
Right arrow Similar articles in PubMed
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Right arrow reprints & permissions
Citing Articles
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Jaakkola, M. S
Right arrow Articles by Jaakkola, J. J. K
Right arrow Search for Related Content
PubMed
Right arrow PubMed Citation
Right arrow Articles by Jaakkola, M. S
Right arrow Articles by Jaakkola, J. J. K


HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
Proc. Am. Thorac. Soc. Am. J. Respir. Cell Mol. Biol.
Copyright © 2006 American Thoracic Society