RGUHS Nat. J. Pub. Heal. Sci Vol No: 9 Issue No: 3 eISSN: 2584-0460
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S Prafulla1 , S Anirudh1 , Gangaborah2 , Prashanth Thankachan3 , Deepa R4 , Eunice Lobo1 , Giridhara R. Babu5
1: Research Fellow, Life course Epidemiology Unit,IIPH Bangalore, Public Health Foundation of India.
2: Consultant (Bio statistician), IIPH Bangalore, Public Health Foundation of India.
3: Associate Professor, Division of Nutrition St Johns Research Institute Bangalore.
4: Indian Institute of Public Health, Public Health Foundation of India, ANV Arcade, 1 Amar Cooperative Society, Kavuri Hills, Madhapur, Hyderabad, India and International Centre for Eye Health, Faculty of Infectious and Tropical Diseases, London School of Hygiene & Tropical Medicine, London, UK.
5: Professor, IIPH Bangalore, Public Health Foundation of India and Wellcome Trust-DBT India alliance Research Fellow in Public Health.
Address for correspondence:
Giridhara R Babu
Professor, Head-Life course Epidemiology,
Public Health Foundation of India,
IIPH-H, Bangalore campus, SIHFW premises,
Beside leprosy hospital, 1st cross, Magadi Road.
Bangalore-560023
Email: epigiridhar@gmail.com
Abstract
Background: Air pollution including ambient air pollution is a global concern attributed to nearly 4.3 million annual deaths worldwide. The model projections based on emission scenarios indicate that this contribution could double by 2050. Ambient fine particulate matter (PM) air pollution is a major risk factor for ill health and death. Our research explores the association between ambient level of particulate matter 2.5(PM2.5) and adverse infant outcomes in capital cities of Low and middle-income countries (LMIC) and high-income countries (HICs).
Objectives: To estimate the level of PM2.5 across selected LMICs and High-income countries (HICs) and to establish/ascertain the predictors of ambient air pollution correlated with adverse infant outcomes.
Methods: Through an ecological study that included data at country-level, from the Global Burden of Diseases 2015, we assessed the exposure to PM2.5 of capital cities of selected LMICs using custom-built software. The primary outcomes of interest were low birth weight, infant mortality rate and the incidence of pneumonia. We developed a linear regression model to evaluate the relationship between mean PM2.5 and the outcomes of interest. In this model, we have controlled for demographic indicators as female literacy rate, smoking habits, usage of solid fuel and exclusive breastfeeding. The data on exposure is the realtime data that we obtained for the year of 2017 but the outcome we have is extracted from the recently published Global Burden of Diseases data of 2015.
Results: Higher levels of PM2.5 levels in the capital cities of LMICsoccurmainly in Dhaka, Bangladesh, Jakarta, Indonesia followed by Hanoi, Vietnam. We found significant association between PM2.5 and Low birth weight, infant mortality however PM2.5 was significantly associated with incidence of Pneumonia. There is limited causal inference due to the ecological nature of the study.
Conclusion: The need for individual-level prospective studies is imperative in nature to determine the causal relationship between the burdensome ambient air pollution and adverse infant outcomes especially in LMICs.
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Introduction
Air pollution (including ambient) is a serious rising global concern that claims almost 3.3 million deaths which are caused annually, with an estimated increase of 50% by 2050.1,2 Majority of the cities in the world have average levels of particulate matters 10 (PM10) and3 2.5 (PM2.5) above the recommended concentrations. In fact the burden of diseases due to ambient PM2.5 outnumbers the combined burden of global health threats such as Malaria and Human Immunodeficiency Virus-Acquired Immunodeficiency Syndrome (HIV-AIDS).4 With the increasingly urban population of the developing world, the environmental air pollutants have also increased exponentially.5, 6 With emissions from the motor vehicles being the main source of ambient air pollution, the vast majority of the urban population breathe polluted air with particulate matter.7 The respiratory consequences are the effect of acute exposure to air pollutants; mortality follows over the long term exposure. Children, elderly, and pregnant women are most susceptible population to air pollution.8 Exposure to ambient air pollutants during pregnancy can have an adverse effect on neonatal birth outcomes and respiratory health.9 The pollutants inhaled by the pregnant mother during pregnancy can cross the alveoli and placental barrier and act directly on developing fetus; can also affect indirectly through systemic changes in the mother leading to a decreased supply of fetal nutrients and oxygen.9 The suggestive mechanism of actions for these changes are oxidative stress,10 interrupted oxygen supply,11,12 decreased DNA methylation, and disturbed hemodynamic response.13-15 Therefore it is possible that exposure to air pollutants perhaps can modulate the immune and inflammatory system leading to epigenetic changes.16-18 Longer exposure to these pollutants during pregnancy may lead to changes in organ development, resulting in complications in later life.19 The maternal and child health outcomes in low and middle-income countries (LMICs) are poorer,20 as 98% of the cities in LMICs do not meet ambient air quality guidelines compared to High-income countries (HICs) where 56% of the cities meet ambient air quality.3 Although several studies have explored adverse birth outcomes and ambient air pollution, there exists a relative dearth of studies that draw firm conclusions about causality on the effect of ambient air pollutants in terms of neonatal outcomes.21 Thus through our study we aim to provide evidence by assessing the magnitude of ambient pollutants concentration and its impact on low birth weight (LBW), mortality, and respiratory morbidities in children. To achieve this, we adopted an interdisciplinary framework to examine our objectives encompassing maternal and child health, environmental health, and big data analytics.
Hence the objectives of our study were, to estimate the level of PM2.5 across selected LMICs and Highincome countries (HICs) and to establish/ascertain the predictors of ambient air pollution correlated with adverse infant outcomes. We hypothesized that countries with high air pollution levels have higher LBW, infant mortality, and the incidence of pneumonia - than countries with low air pollution levels.
Materials and Methods
Study design and study population
An ecological study using aggregate data from population-level rather that individuals was conducted using data for the year 2017 from 10 countries: six LMICsand four HICs as seen in Table 1. Countries were classified based on the World Bank Atlas method22 of Gross National Income(GNI) per capita - LMICs: between $1,006 to$3955, and as HICs: $12,235 or more.23 Based on relatively low amounts of data regarding exposure to ambient air pollutants and its effect on neonatal outcome the following countries were finalized for the study: LMICs - India, Bangladesh, El Salvador, Ethiopia, Indonesia, Nepal, Philippines, Uganda and Vietnam; and HICs - United States of America (USA), United Kingdom(UK), United Arab Emirates(UAE), and China. HICs were chosen to compare the pollution data with LMIC countries.
Exposure assessment;
The exposure to air pollutants was collected using an advanced software system and program, retrieved live on an hourly-basis automatically from the Plume Labs Application Program Interface (API). Plume Lab that tracks air pollution and captures metrics on absolute concentration of major harmful atmospheric pollutants over 60 countries across the global. It provides real time information and projections for the next 24 hours as well. However, only 10 countries had data available for PM2.5 levels. For our study, we built a technical software system that has three subsystems: i) data capturing - to obtain data scheduled from the API; ii) input processing - to process stored data, filters and stores in the Microsoft Azure database, iii) reporting - that aggregates the stored data and generates reports in Microsoft excel format and transmits the reports to the research team through periodic emails. The data of hourly intervals throughout 24 hours in a day for all locations were stored in the Microsoft Azure database (The statistical analysis and visual analytics were made using these reports. Data extraction process began on August 10th, 2017 and continued until October 15th, 2017 - the last day of UN Data Challenge for Climate Change. The time stamp for online data collection was uniform across all countries. Therefore, the analysis of air pollutants included the measurement and analysis of the air pollutants over 56 days.
Outcome assessment;
The primary outcome of interest was low birth weight (LBW) while the secondary outcomes were infant mortality rate (IMR) and the incidence of pneumonia. The recently published reports on the same were used to extract. These included the World Bank data from 201524 for LBW, and the Global Burden of Diseases (GBD) 2015 data for secondary outcomes.25 The GBD uses different sources to populate the information. Most information comes from the data providers like International Household survey network, Integrated Public Use Micro data Series International, (IPUMS-I), IPUMSUSA, Simple Online Data Archive for Population Studies (SodaPop), Synapse (Sage Bionetwork repository) and Health Data. Gov. The data on infant mortality and incidence of pneumonia have been included from the Global Health Data exchange that includes GDB data.25
Confounders;
Based on available evidence, we included the proportion of households using solid fuels; as this is both related to air pollution levels and adverse health outcome26-31, smoking history in women was included,32-37 female literacy was chosen as a confounder as literacy has shown to reduce in LBWincidence and also has impact on bringing down household air pollution,38-43 proportion of children exclusively breastfed for 6 months,44,45,46,47 as confounders. The data were extracted from the Health, Nutrition and Population Statistics48 for all the countries. The confounders were adjusted during analysis and tested for their effect of interaction on PM2.5. We also included temperature49-56 and humidity57-60 as confounders Weather Data was collected manually from a single source for all locations using a website (www. timeanddate.com).
Statistical analysis;
The data were analyzed using SPSS software version 23. The dependent and independent variables have checked for normality. The descriptive statistics were reported. The association between PM2.5 and LBW, IMR and incidence of pneumonia were quantified using univariate and Multiple Linear Regression. Before proceeding to the regression analysis the assumptions of linear regression were tested.
Results
The mean PM2.5 levels of the respective countries are shown in table-1 for the 56 days of the data extraction period. As seen in the table, the mean level of PM2.5 was highest in Indonesia and Bangladesh followed by Ethiopia and India among the LMICs and in China among HICs. El Salvador (LMIC) and USA (HIC) had minimum levels of PM2.5
We further conducted univariate and multivariate linear regression analyses to understand the relationship between PM2.5 and selected adverse infant outcomes. Univariate analysisin Table 2 showed no significant association between PM2.5 level with LBW and IMR however there was significant association with incidence of pneumonia.Thefactors as female literacy,smoking habits of women, use of solid fuels, and exclusive breastfeeding rate have been adjusted in the multivariate model. Beta coefficient, 95% confidence interval and p-value are reported in table 3. The multivariate linear regression analysis results show no relationship between PM2.5 levels with LBW and IMR. There was significant association between mean PM2.5 levels and incidence of pneumonia even after adjusting for confounders.
Discussion
The results of our study that included data from Lower and middle-income countries (LMIC) and high-income countries (HICs) suggests that exposure to the ambient level of PM2.5 is not associated with low birth weight, infant mortality,with the exception of mean level of PM2.5 that has shown significant correlation with incidence of pneumonia.
By means of our ecological study that provides a cursory view through country-level data, our results suggests a greater burden of ill health related to environmental pollution. Therefore, we strongly recommend the exploration further through more studies to fill the knowledge gaps regarding the consequences of adverse infant outcomes and exposure to PM2.5. We advocate the need for prospective cohort studies as a key research approach with good precision and sample size to re-confirm the evidence at individual-level.
For our primary outcome, the results of our study contradicted previous studies across the globe that reported a positive association between PM2.5 and low birth weight.61-63 Further studies by Muhammad et al found that exposure to particulate matter is associated with the decreased birth weight,64 whileConnieng et al also examined the increased risk for low birth weight with an increase in exposure to PM2.5. A retrospective cohort done in China showed that exposure to an incremental dose of 10 μg/m3 was associated with the decrease in birth weight by 4.94gm.65 The difference in inferences may be due to the inclusion of only a few selected countries (which had the data available on PM2.5 in the regression analysis and might be due to the population level data and not individual level PM2.5 data that we have considered to evaluate the relationship with the adverse infant outcome.
Our results with respect to infant mortality show ambient level of PM2.5 was not associated with Infant mortality. However, there is not enough of available studies to support our evidence on the association between PM2.5 andneonatal mortality rate (NMR). The majority of the studies are based on post-neonatal mortality and under five mortality. We also found inconsistency with the available, limited sources of evidence. The study done in the United States on estimating the exposure of particulate matter with respect to the death of a cohort of infants observed that particulate matter is associated with increased risk of post-neonatal mortality.66 while two other studies in California showed an increase in 5% risk for respiratory-related deaths among infants due to exposure to the particulate matter;67 and reported the relationship between long-term exposure to PM2.5 air pollution and post-neonatal infant death in all areas of California.68
The role of PM2.5 with respect to the incidence of pneumonia has been found significant. A study done in China shows increased risk of childhood pneumonia associated with particulate matter;69-70 while developing countries showed positive association between air pollution and incidence of upper- and lower-respiratory infections in children.71 and association with hospitalization due to Pneumonia.72
Strength and limitations:
In light of our findings our study had certain several strengths and limitations. One of the major strength of our study is that we have adjusted the possible covariates including health indicators in our analysis. Using the data made available by United Nations climate action team, we were able to offer inputs for further studies and policy support. Through our study, we show that it is possible to address modifiable risk factor such as air pollution using the big data analytics, and thereby, contribute towards at alleviating the ill health in infants and children.
Limitations include: use of country-level data since an ecological study was undertaken for a shorter duration. The data on exposure is the real-time data that we obtained for the year of 2017 but the outcome is extracted from the recently published Global Burden of Diseases data of 2015. We have analyzed the data with an assumption thatthe current level of ambient PM2.5 will be similar in the year 2015. Hence, the causal inference could not be made. Other than this, the size of the sample we have chosen is small hence study results cannot be generalized. We have not adjusted for smoking status of men within the household and this is a limitation of this study.
Conclusion: The overall Infant health indicators seemed to be very poor in LMICs compared to HICs. In spite of this, the level of pollution is also becoming a major concern. As per the data collected from different capital cities of LMIC countries, it seems that the level of ambient PM2.5 is higher in lower and middleincome countries. If we glance at the child health indicators we can observe that there are still many lower and middle-income countries with poor infant outcomes.
We have not observed a significant association between ambient PM2.5 and any of the outcome indicators after controlling for the covariates. Hence, we recommend a future prospective study to confirm the association by assessing the individual exposure during pregnancy and its impact on infant health outcome.
Funding: No funding support received. Dr. Giridhara Babu was accepted to participate in the Data for Climate Action Challenge and was provided with access to data on air pollutants in real time.
Supporting File
References
1. Lelieveld, J., et al., The contribution of outdoor air pollution sources to premature mortality on a global scale. Nature, 2015. 525(7569): p. 367- 371.
2. Landrigan, P.J., et al., The Lancet Commission on pollution and health. The Lancet, 2017.
3. Organization, W.H., WHO global urban ambient air pollution database (update 2016). Geneva. Diunduh, 2016.
4. Apte, J.S., et al., Addressing global mortality from ambient PM2. 5. Environmental science & technology, 2015. 49(13): p. 8057-8066.
5. Samajdar, P., Air pollution is now the fifth largest killer in India, says newly released findings of Global Burden of Disease report.
6. Kindzierski, W.B., Ambient Air Quality Data Summary and Trend Analysis, in Part I Main Report. 2009, Wood Buffalo Environmental Association.
7. Pollution, H.E.I.P.o.t.H.E.o.T.-R.A., Trafficrelated air pollution: a critical review of the literature on emissions, exposure, and health effects. 2010: Health Effects Institute.
8. Organization, W.H., Health effects of particulate matter. Policy implications for countries in Eastern Europe. Caucasus and central Asia. World Health Organization Regional Office for Europe, Copenhagen, 2013.
9. Kannan, S., et al., Exposures to airborne particulate matter and adverse perinatal outcomes: a biologically plausible mechanistic framework for exploring potential. Ciencia & saude coletiva, 2007. 12(6): p. 1591-1602.
10. Siddiqui, A.R., et al., Prenatal exposure to wood fuel smoke and low birth weight. Environmental health perspectives, 2008. 116(4): p. 543.
11. Kim, K.-H., S.A. Jahan, and E. Kabir, A review of diseases associated with household air pollution due to the use of biomass fuels. Journal of hazardous materials, 2011. 192(2): p. 425-431.
12. Dejmek, J., et al., The impact of polycyclic aromatic hydrocarbons and fine particles on pregnancy outcome. Environmental health perspectives, 2000. 108(12): p. 1159.
13. Currie, J. and M. Neidell, Air pollution and infant health: what can we learn from California's recent experience? The Quarterly Journal of Economics, 2005. 120(3): p. 1003- 1030.
14. de Melo, J.O., et al., Inhalation of fine particulate matter during pregnancy increased IL-4 cytokine levels in the fetal portion of the placenta. Toxicology letters, 2015. 232(2): p. 475-480.
15. Slama, R., et al., Meeting report: atmospheric pollution and human reproduction. Environmental health perspectives, 2008. 116(6): p. 791.
16. Li, Y.-F., et al., Maternal and grandmaternal smoking patterns are associated with early childhood asthma. Chest Journal, 2005. 127(4): p. 1232-1241.
17. Li, N., et al., Ultrafine particulate pollutants induce oxidative stress and mitochondrial damage. Environmental health perspectives, 2003. 111(4): p. 455.
18. Ji, H. and G.K.K. Hershey, Genetic and epigenetic influence on the response to environmental particulate matter. Journal of Allergy and Clinical Immunology, 2012. 129(1): p. 33-41.
19. Kajekar, R., Environmental factors and developmental outcomes in the lung. Pharmacology & therapeutics, 2007. 114(2): p. 129-145.
20. Amiri, A. and U.-G. Gerdtham, Impact of maternal and child health on economic growth: New evidence based granger causality and DEA analysis. Newborn and Child Health, Study Commissioned by the Partnership for Maternal, Lund University, Sweden, 2013.
21. Šrám, R.J., et al., Ambient air pollution and pregnancy outcomes: a review of the literature. Environmental health perspectives, 2005. 113(4): p. 375-382.
22. GNI per capita, Atlas method (current US$). 2017.
23. Country classifications, in Data sources, country classifications and aggregation methodology. 2018.
24. Low-birthweight babies (% of births). 2012, World Bank.
25. Global Burden of Disease Study 2015 (GBD 2015) Stillbirths, Neonatal, Infant, and Under-5 Mortality 1980-2015. 2015, Institute for Health Metrics and Evaluation.
26. Siddiqui, A.R., et al., Indoor air pollution from solid fuel use and low birth weight (LBW) in Pakistan. Epidemiology, 2005. 16(5): p. S86.
27. Pope, D.P., et al., Risk of low birth weight and stillbirth associated with indoor air pollution from solid fuel use in developing countries. Epidemiologic reviews, 2010. 32(1): p. 70-81.
28. Patel, A.B., et al., Impact of exposure to cooking fuels on stillbirths, perinatal, very early and late neonatal mortality-a multicenter prospective cohort study in rural communities in India, Pakistan, Kenya, Zambia and Guatemala. Maternal health, neonatology and perinatology, 2015. 1(1): p. 18.
29. Khan, M.N., et al., Household air pollution from cooking and risk of adverse health and birth outcomes in Bangladesh: a nationwide population-based study. Environmental Health, 2017. 16(1): p. 57.
30. Kelly, M.S., et al., The effect of exposure to wood smoke on outcomes of childhood pneumonia in Botswana. The International Journal of Tuberculosis and Lung Disease, 2015. 19(3): p. 349-355.
31. Dherani, M., et al., Indoor air pollution from unprocessed solid fuel use and pneumonia risk in children aged under five years: a systematic review and meta-analysis. Bulletin of the World Health Organization, 2008. 86: p. 390-398C.
32. Dessì, A., et al., Exposure to tobacco smoke and low birth weight: from epidemiology to metabolomics. Expert review of proteomics, 2018(just-accepted).
33. Simpson, R.J. and N.A. Smith, Maternal smoking and low birthweight: implications for antenatal care. Journal of Epidemiology & Community Health, 1986. 40(3): p. 223-227.
34. Wisborg, K., et al., Exposure to tobacco smoke in utero and the risk of stillbirth and death in the first year of life. American journal of epidemiology, 2001. 154(4): p. 322-327.
35. Kleinman, J.C., et al., The effects of maternal smoking on fetal and infant mortality. American Journal of Epidemiology, 1988. 127(2): p. 274-282.
36. Gilliland, F.D., et al., Effects of early onset asthma and in utero exposure to maternal smoking on childhood lung function. American journal of respiratory and critical care medicine, 2003. 167(6): p. 917-924.
37. Taylor, B. and J. Wadsworth, Maternal smoking during pregnancy and lower respiratory tract illness in early life. Archives of disease in childhood, 1987. 62(8): p. 786-791.
38. Muula, A., S. Siziya, and E. Rudatsikira, Parity and maternal education are associated with low birth weight in Malawi. African health sciences, 2011. 11(1).
39. Chevalier, A. and V. O'Sullivan, Mother's education and birth weight. 2007.
40. Shetty, A. and S. Shetty, The Impact of Female Literacy on Infant Mortality Rate in Indian States. Current Pediatric Research, 2014. 18(1).
41. Kateja, A., Role of female literacy in maternal and infant mortality decline. Social Change, 2007. 37(2): p. 29-39.
42. Nirmolia, N., et al., Prevalence and risk factors of pneumonia in under five children living in slums of Dibrugarh town. Clinical Epidemiology and Global Health, 2018. 6(1): p. 1-4.
43. Rudan, I., et al., Epidemiology and etiology of childhood pneumonia. Bulletin of the world health organization, 2008. 86: p. 408-416B.
44. Biks, G.A., et al., Exclusive breast feeding is the strongest predictor of infant survival in Northwest Ethiopia: a longitudinal study. Journal of Health, Population and Nutrition, 2015. 34(1): p. 9.
45. Chandhiok, N., et al., Changes in exclusive breastfeeding practices and its determinants in India, 1992–2006: analysis of national survey data. International breastfeeding journal, 2015. 10(1): p. 34.
46. Lamberti, L.M., et al., Breastfeeding for reducing the risk of pneumonia morbidity and mortality in children under two: a systematic literature review and meta-analysis. BMC public health, 2013. 13(3): p. S18.
47. Boccolini, C.S., et al., Breastfeeding can prevent hospitalization for pneumonia among children under 1 year old. Jornal de pediatria, 2011. 87(5): p. 399-404.
48. Perera, F., Pollution from Fossil-Fuel Combustion is the Leading Environmental Threat to Global Pediatric Health and Equity: Solutions Exist. International journal of environmental research and public health, 2017. 15(1): p. 16.
49. Murray, L.J., et al., Season and outdoor ambient temperature: effects on birth weight1. Obstetrics & Gynecology, 2000. 96(5): p. 689- 695.
50. Strand, L.B., A.G. Barnett, and S. Tong, The influence of season and ambient temperature on birth outcomes: a review of the epidemiological literature. Environmental research, 2011. 111(3): p. 451-462.
51. Elter, K., et al., Exposure to low outdoor temperature in the midtrimester is associated with low birth weight. Australian and New Zealand journal of obstetrics and gynaecology, 2004. 44(6): p. 553-557.
52. Mullany, L.C., et al., Risk of mortality associated with neonatal hypothermia in southern Nepal. Archives of pediatrics & adolescent medicine, 2010. 164(7): p. 650-656.
53. Auger, N., et al., Ambient heat and sudden infant death: a case-crossover study spanning 30 years in Montreal, Canada. Environmental health perspectives, 2015. 123(7): p. 712.
54. Sodemann, M., et al., Hypothermia of newborns is associated with excess mortality in the first 2 months of life in Guinea-Bissau, West Africa. Tropical Medicine & International Health, 2008. 13(8): p. 980-986.
55. Bull, G., The weather and deaths from pneumonia. The Lancet, 1980. 315(8183): p. 1405-1408.
56. Lin, H.-C., et al., Seasonality of pneumonia admissions and its association with climate: an eight-year nationwide population-based study. Chronobiology international, 2009. 26(8): p. 1647-1659.
57. Barreca, A.I., Climate change, humidity, and mortality in the United States. Journal of Environmental Economics and Management, 2012. 63(1): p. 19-34.
58. Ou, C.Q., et al., The impact of relative humidity and atmospheric pressure on mortality in Guangzhou, China. Biomedical and Environmental Sciences, 2014. 27(12): p. 917- 925.
59. Tasci, S.S., C. Kavalci, and A.E. Kayipmaz, Relationship of Meteorological and Air Pollution Parameters with Pneumonia in Elderly Patients. Emergency medicine international, 2018. 2018.
60. Ning, X., L. Xiao-Mei, And L. Rong-Jun, Study On The Relationship Between Pneumonia And Meteorological Factors In Qingdao Urban Area [J]. Medical Journal of Qilu, 2007. 2: p. 003.
61. Maisonet, M., et al., Relation between ambient air pollution and low birth weight in the Northeastern United States. Environmental Health Perspectives, 2001. 109(Suppl 3): p. 351.
62. Fleischer, N.L., et al., Outdoor air pollution, preterm birth, and low birth weight: analysis of the world health organization global survey on maternal and perinatal health. Environmental health perspectives, 2014. 122(4): p. 425.
63. Bell, M.L., K. Ebisu, and K. Belanger, Ambient air pollution and low birth weight in Connecticut and Massachusetts. Environmental health perspectives, 2007. 115(7): p. 1118.
64. Salam, M.T., et al., Birth outcomes and prenatal exposure to ozone, carbon monoxide, and particulate matter: results from the Children’s Health Study. Environmental health perspectives, 2005. 113(11): p. 1638.
65. Han, Y., et al., Effects of particulate matter exposure during pregnancy on birth weight: A retrospective cohort study in Suzhou, China. Science of The Total Environment, 2018. 615: p. 369-374.
66. Woodruff, T.J., J. Grillo, and K.C. Schoendorf, The relationship between selected causes of postneonatal infant mortality and particulate air pollution in the United States. Environmental health perspectives, 1997. 105(6): p. 608.
67. Ritz, B., M. Wilhelm, and Y. Zhao, Air pollution and infant death in southern California, 1989– 2000. Pediatrics, 2006. 118(2): p. 493-502.
68. Woodruff, T.J., J.D. Parker, and K.C. Schoendorf, Fine particulate matter (PM2. 5) air pollution and selected causes of postneonatal infant mortality in California. Environmental Health Perspectives, 2006. 114(5): p. 786.
69. Fuertes, E., et al., Associations between particulate matter elements and early-life pneumonia in seven birth cohorts: results from the ESCAPE and TRANSPHORM projects. International journal of hygiene and environmental health, 2014. 217(8): p. 819-829.
70. Lu, C., et al., Effects of ambient air pollution on the prevalence of pneumonia in children: Implication for National Ambient Air Quality Standards in China. Indoor and Built Environment, 2014. 23(2): p. 259-269.
71. Romieu, I., et al., Outdoor air pollution and acute respiratory infections among children in developing countries. Journal of Occupational and Environmental Medicine, 2002. 44(7): p. 640-649.
72. Patto, N.V., et al., Exposure to fine particulate matter and hospital admissions due to pneumonia: Effects on the number of hospital admissions and its costs. Revista da Associação Médica Brasileira, 2016. 62(4): p. 342-346.