Abstract
Objective
Smoke from burning of biomass fuels has been linked with adverse pregnancy outcomes and with hypertension among nonpregnant subjects; association with hypertension during pregnancy has not been well studied. We sought to evaluate whether use of wood cooking fuel increases the risk of maternal hypertension at delivery compared to gas which burns with less smoke.
Methods
Information on fuel use and blood pressure was available for analysis from a cross-sectional survey of 1369 pregnant women recruited at delivery in India.
Results
Compared to gas users, women using wood as fuel had on average lower mean arterial pressure (adjusted effect size −2.0 mmHg; 95% CI −3.77, −0.31) and diastolic blood pressure (adjusted effect size −1.96 mmHg; 95% CI −3.60, −0.30) at delivery. Risk of hypertension (systolic > 139 mmHg or diastolic > 89 mmHg) was 14.6% for women cooking with wood compared to 19.6% for those cooking with gas although this did not reach significance after adjustment, using propensity score techniques, for factors that make wood and gas users distinct (adjusted prevalence ratio 0.76; 95% CI 0.49, 1.17).
Conclusions
Combustion products from the burning of biomass fuels are similar to those released with tobacco smoking which has been linked with a reduced risk for preeclampsia. The direction of our findings suggests the possibility of a similar effect for biomass cook smoke. Whether clean cook cooking interventions being promoted by international advocacy organizations will impact hypertension in pregnancy warrants further analysis as hypertension remains a leading cause of maternal death worldwide and cooking with biomass fuels is widespread.
Keywords: biomass cook smoke, pregnancy, hypertension, gestational hypertension, household air pollution
INTRODUCTION
Biomass fuels such as wood, charcoal, and crop residues are the primary energy source for cooking and/or heating for an estimated 2.8 billion people, almost half of the world’s population.1 Air pollution generated from the inefficient combustion of these solid fuels has been recognized as a major contributor to the global burden of disease. Recent estimates suggest that smoke generated from biomass burning accounts for over 4 million premature deaths among children and adults from pneumonia, lung cancer, chronic lung disease or cardiovascular disease.2,3 More than a quarter (27%) of the people using solid fuels worldwide resides in India.4
For women and girls globally, household air pollution ranks as the second most important risk factor contributing to disability-adjusted life years lost.2 As women of reproductive age are the primary cooks in many households, there has been increasing attention devoted to the potential adverse effects of household air pollution on pregnancy outcomes. Observational studies suggest that biomass smoke exposure during pregnancy may decrease birth weight and increase the risk of low birth weight and stillbirth.5–12 We have also reported an increased risk of preterm birth among Indian women cooking with wood during pregnancy compared to those cooking with gas.13
Despite a growing focus on birth outcomes following exposure to household air pollution, little attention has been devoted to maternal outcomes. A family of pregnancy complications that might plausibly be linked with cooking smoke is hypertensive disorders of pregnancy which includes preeclampsia/eclampsia, gestational hypertension, and chronic hypertension with or without superimposed preeclampsia. Household air pollution from biomass burning has been linked with both increases in blood pressure14,15 and chronic hypertension16–18 among nonpregnant populations in several observational cohorts. Introduction of an improved cook stove reduced diastolic blood pressure among Guatemalan cooks20 and reduced systolic blood pressure among older cooks in a recent Nicaraguan trial.21 No studies have evaluated the risk of gestational hypertesion or preeclampsia/eclampsia among women cooking with biomass fuels although outdoor air pollution has been associated with an increased risk of gestational hypertension in most22–28 but not all studies.29,30 This is in contrast to the well documented decreased risk for preeclampsia among cigarette smokers.31 Since hypertension is a major cause of maternal death32, it is critical to determine whether pollution generated from the burning of biomass fuels affects this risk. Policymakers will want to know whether efforts to increase the number of households cooking with clean energy might translate into a reduction in maternal deaths from hypertension.
We used data from two similarly conducted cross sectional surveys of pregnant women enrolled at delivery in India to evaluate the relationship between hypertension in pregnancy and wood cooking fuel, as a marker of household air pollution from biomass burning. Due to the fairly rudimentary delivery settings, information about proteinuria and other end organ involvement was not available; consequently, we were limited in our ability to distinguish between the various hypertensive disorders of pregnancy. Measured hypertension in our cohort therefore represents a mix of preeclampsia/eclampsia, gestational hypertension, and underlying chronic hypertension.
We recognize that women cooking with wood are likely to be systematically poorer than women who cook with gas. An identified association between cooking fuel and hypertension could therefore be biased by these socioeconomic factors as has been suggested in our previous work with regards to low birth weight and other birth outcomes.13 We employed propensity score techniques to address this concern and to increase the statistical power to simultaneously adjust for multiple confounders.33
METHODS
Study Sites/Procedures
Information regarding self-reported primary cooking fuel, time spent cooking and maternal blood pressure measurements was available for secondary analysis from two cross-sectional studies of pregnant women in central east India that were conducted to establish the burden of malaria during pregnancy.34,35 In these two studies, all women aged 15 years or older who presented for delivery at the study sites were approached for consent. Enrollment occurred over twelve months in Jharkhand state beginning in December 2006 at one urban and two rural facilities. In neighboring Chhattisgarh, recruitment occurred from June 2007 to May 2008 in two urban and two rural facilities. As case report forms and study procedures were the same in both cohorts, data were concatenated from the two sites to increase power and generalizability of this secondary analysis.
Following consent, women were interviewed about a variety of demographic, economic, obstetric and medical factors. Information obtained included the primary cooking fuel used in their household and average number of hours per day they spent cooking during their pregnancy. A physical examination was performed which included measurement of blood pressure, height and weight. For blood pressure, trained research staff followed a standardized protocol using an appropriately sized cuff with the subject’s arm supported at the level of the heart. The systolic blood pressure (SBP) was recorded as the mmHg visible on the mercury manometer when the pulse was first auscultated. The diastolic blood pressure (DBP) was recorded when the auscultated pulse disappeared. The blood pressure measurements were repeated twice per subject by the same research staff and averaged to represent the SBP and DBP. The history and physical examination occurred at a convenient time after admission to the ward and before 24 hours had lapsed since delivery. The maternal physical examination occurred after delivery for over 87% of the subjects. We therefore limited analyses to women with postpartum measurements of blood pressure to represent a more uniform sample as intrapartum measurements may be elevated during contractions or from pain. Vital signs during the course of the labor and delivery were neither consistently obtained nor recorded by the managing clinical team. Blood pressure measurements were consequently limited to those obtained by research staff. Further details of the original studies less relevant to this analysis are presented elsewhere.34–37
Definitions
A subject’s body mass index (BMI) was calculated by dividing her weight in kilograms at the time of the physical examination by her height in meters squared: BMI=weight (in kilograms)/ height (in meters2). Hypertension at delivery (HTN) was defined as a SBP of greater than 139 mmHg or a DBP of greater than 89 mmHg. Severe hypertension at delivery (severe HTN) was defined as a SBP of greater than 159 mmHg or a DBP of greater than 109 mmHg. Information about maternal proteinuria was not uniformly available in the cohort; this was consequently not used in our definition of hypertension at delivery. Mean arterial pressure (MAP) was calculated using the SBP and DBP measurements as follows: MAP= (2/3*DBP) + (1/3*SBP). Nulliparity was defined as having delivered no prior infant after the onset of fetal quickening, whether or not the infant was born alive or stillborn.
Data Analysis
We restricted our analyses to a comparison of women cooking with wood to those cooking with gas rather than including a broader range of potentially non-comparable fuel types38–40 (charcoal, cow dung, kerosene) as wood and gas were used by more than 90% of women in our cohort.
Propensity- score model
To address the systematic differences between women cooking with wood versus gas, a propensity score model was fit. Women who primarily cooked with wood were compared to women cooking with gas across a number of variables that were potentially linked with exposure (wood cooking fuel) but which might be confounded by poverty. Odds ratios and c-statistics were calculated to explore the association of each covariate with wood fuel use. The final variables for the propensity score model were chosen based on the strength of the association and the prevalence of the predictor. A propensity score was then calculated for each subject using this model which represents the predicated probability that the subject’s primary household fuel was wood (range 0 to 1). We excluded from the propensity score modeling exercise obstetric or medical covariates that might be more strongly linked with hypertensive outcomes and instead considered these variables for inclusion separately in the final adjusted models. Exploration of the relationship between HTN and the propensity score suggested that the propensity score should be modeled nonlinearly. The propensity score was categorized into quintiles for multivariable modeling and can loosely be interpreted as a proxy for poverty.
Unadjusted association between fuel use and HTN
The proportions of subjects with HTN and severe HTN as well as the mean SBP, DBP, and MAP were compared between the two groups (users of wood versus gas). Categorical data are presented as frequency counts (percent) and compared using the Pearson chi-square or Fisher’s exact as appropriate. Continuous data are summarized as means (± standard deviation) and compared using analysis of variance. Unconditional log-binomial regression models were constructed to estimate univariable prevalence ratios and associated 95% confidence intervals (CIs) for HTN. The referent group was women cooking primarily with gas. Exact logistic regression was used to estimate an odds ratio for severe HTN given the rarity of this outcome. Linear regression models were used to estimate the effect of wood fuel exposure on mean DBP, SBP, and MAP; 95% CIs were constructed using the modeled standard error.
Adjusted association between fuel use and HTN
Variables that might be plausibly linked with HTN were considered for inclusion in adjusted models by evaluating their univariate association with HTN. These covariates included maternal age, body mass index, nulliparity, multiple gestations, history of hypertension, history of diabetes mellitus, adequate antenatal clinic attendance (4 or more visits), maternal smoking, use of smokeless tobacco, and parasitemia. We also considered the presence of windows and the time spent cooking for potential inclusion as these might reflect exposure to cooking smoke. While the range of responses varied from 1 to 7 hours, almost all of the variability was limited to the upper decile of cooking time (4 or more hours of cooking). We therefore dichotomized time spent cooking into 4 or more hours versus less than 4 hours.
Multivariable log-binomial regression modeling was used to adjust the association of wood fuel use with HTN for the categorized propensity score, and variables we identified to be associated with HTN at a significance level of 0.05 or less. A final adjusted prevalence ratio and 95% CI was calculated based on these findings. The effect of fuel use on SBP, DBP and MAP was adjusted in multivariable linear regression using the same covariates chosen in the final adjusted HTN model. No adjustments were made to the severe HTN model given the rarity of this outcome. Data were missing for fewer than 5 subjects for the covariates included in the final model and therefore no additional methods were employed to handle missing data.
Statistical analyses were performed using SAS software version 9.2 (Cary, North Carolina).
Ethical Clearance
The study was approved by the Boston University and Centers for Disease Control and Prevention Institutional Review Boards, the Ethics committee and the Scientific Advisory Committee of the National Institute of Malaria Research in India, and the Health Ministry Screening Committee of Indian Council of Medical Research.
RESULTS
In the state of Jharkhand, a total of 739 pregnant women were screened at the time of delivery and all were eligible, although 21 declined participation. In the state of Chhattisgarh, all 1028 pregnant women screened were eligible; two women declined participation leaving a combined total of 1744 subjects from the two cohorts. For this analysis, we excluded two women for lack of blood pressure measurements, 174 women that did not use wood or gas as their primary fuel, and an additional 199 women that had only intrapartum blood pressure measurements recorded. A total of 1369 subjects remained, 1134 who cooked primarily with wood and 235 who cooked primarily with gas. Our decision to limit analysis to postpartum measurements of blood pressure was affirmed by the finding that the diagnosis of HTN was remarkably high among women with intrapartum measurements (66 of 195 subjects, 33.9%) compared with those who had postpartum measurements (212 of 1369, 15.5%; p<0.0001).
Comparison of wood and gas users and propensity score model
As anticipated, women who primarily cooked with wood were quite different than women cooking with gas (Table 1). They were less likely to be overweight, to have attended an adequate number of antenatal clinic visits, and to be taking iron and folate. With the exception of marital status, women cooking with wood differed across every socio-demographic characteristic we considered. They were more likely to be from a historically disadvantaged caste, to work in agricultural occupations, and to live in dwellings made with impermanent wall, roof, and floor materials. They were less likely to have completed more than 5 years of school, to own modern material comforts, or to have windows in their homes.
Table 1.
Wood groupa n=1134 |
Gas groupa n=235 |
Significance p-value |
|
---|---|---|---|
Cohortb | |||
Jharkhand Chhattisgarh |
389 (34.3%) 745 (65.7%) |
80 (34.0%) 155 (66.0%) |
0.9389 |
Time spent cooking | |||
Upper decile of daily cook time | 202 (17.8%) | 21 (8.9%) | 0.0008 |
Ventilation | |||
House has windowsb | 749 (66.1%) | 211 (89.8%) | <0.0001 |
Maternal and pregnancy characteristics | |||
Age < 20 yearsc | 88 (7.8%) | 10 (4.3%) | 0.0579 |
Overweight (BMI ≥ 25) | 17 (1.5%) | 8 (3.4%) | 0.0471 |
Underweight (BMI ≤ 18.5) | 196 (17.3%) | 29 (12.3%) | 0.0627 |
Primiparous | 602 (53.1%)) | 123 (52.3%) | 0.8348 |
Multiple gestation | 14 (1.2%) | 1 (0.4%) | 0.4900 |
History of hypertensionb | 14 (1.2%) | 3 (1.3%) | 1.000 |
Maternal habits | |||
Smokes | 2 (0.2%) | 0 (0%) | 1.000 |
Use of smokeless tobaccob | 328 (28.9%) | 11 (4.7%) | <0.0001 |
Drinks alcohol | 23 (2.0%) | 1 (0.4%) | 0.1034 |
Medical and obstetric history | |||
Adequate antenatal visits (≥4) | 381 (33.8%) | 146 (62.1%) | <0.0001 |
Taking iron | 870 (76.7%) | 206 (87.7%) | 0.0002 |
Taking folate | 817 (72.1%) | 197 (83.8%) | 0.0002 |
History of diabetes | 2 (0.2%) | 0 (0%) | 1.000 |
History of hypertensionb | 14 (1.2%) | 3 (1.3%) | 0.9578 |
Multiple gestation | 14 (1.2%) | 1 (0.4%) | 0.2782 |
Placental or peripheral parasitemia at delivery | 42 (3.7%) | 7 (3.0%) | 0.5724 |
Socio-demographic characteristicsd | |||
Married | 1132 (99.8%) | 235 (100.0%) | 1.0000 |
Historically disadvantaged castee | 992 (87.6%) | 133 (56.6%) | <0.0001 |
Agricultural work | 266 (23.5%) | 7 (3.0%) | <0.0001 |
Formal schooling ≤ 5 years | 643 (56.7%) | 40 (17.02%) | <0.0001 |
Impermanent/semi-permanent roof | 1095 (96.6%) | 93 (39.67%) | <0.0001 |
Impermanent/semi-permanent floor | 991 (87.4%) | 34 (14.5%) | <0.0001 |
Impermanent/semi-permanent wall | 1000 (88.2%) | 37 (15.7%) | <0.0001 |
Owns radio | 267 (23.5%) | 128 (54.5%) | <0.0001 |
Owns electric fan | 364 (32.1%) | 214 (91.1%) | <0.0001 |
Owns room cooler | 45 (4.0%) | 120 (51.1%) | <0.0001 |
Owns televisionb | 363 (32.0%) | 210 (89.4%) | <0.0001 |
Owns refrigerator | 6 (0.5%) | 70 (29.8%) | <0.0001 |
Owns motorcycle | 131 (11.6%) | 147 (62.6%) | <0.0001 |
Owns 4 wheel vehicle | 14 (1.2%) | 29 (12.3%) | <0.0001 |
Propensity scoref | 0.93 (±0.14) | 0.32 (±0.32) | <0.0001 |
Values represent n (%) or mean (± standard deviation).
Significantly associated with hypertension (p <0.05)
Age categorized as many women unable to recall their birth date.
Considered for inclusion in propensity score model.
Historically disadvantaged castes include Scheduled Caste, Other Backward Caste, and Scheduled Tribes.
Propensity score model: Propensity to use wood=0.3155 + (0.76896*impermanent walls) + (0.3473*impermanent floors) + (0.6156*impermanent roof) + (0.3952*member of historically disadvantaged caste) + (0.2099*primary school education or less) + (0.5277*agricultural occupation) − (0.0444* owns radio) − (0.5265*owns electric fan) − (0.6554*owns room cooler) − (0.1104*owns television) − (0.5265*owns refrigerator) + (0.0923*owns 4 wheel vehicle).
To address these systematic differences between women cooking with wood versus gas, a propensity score model was created. The model fit included 13 variables with a c-statistic of 0.951; the variables were impermanent roofing, impermanent walls, impermanent floors, caste, agricultural work, primary education, and ownership of a radio, electric fan, room cooler, television, refrigerator, motorcycle and four wheel vehicle. The mean propensity score among wood users was 0.93 and among gas users was 0.32 (p<0.0001).
Univariable association of wood fuel use with hypertension and blood pressure
Compared to women cooking with gas, 14.6% of women using wood as their primary fuel met criteria for HTN at delivery compared to 19.6% of gas users (p=0.0570); prevalence ratio 0.75 [95% CI 0.56, 1.00]) (Table 2). Mean DBP and MAP following delivery was significantly lower among women cooking with wood compared to those cooking with gas (p=0.001 and p=0.0072 respectively, Table 2). The effect size for both DBP and MAP was less than 5 mmHg. There was no difference in the frequency of severe HTN or in mean SBP between the two groups.
Table 2.
Wood groupa n=1134 |
Gas groupa n=235 |
Unadjusted effect size [95% CI] |
|
---|---|---|---|
HTN | 166 (14.6%) | 46 (19.6%) | 0.75 [0.56, 1.00]b |
Severe HTN | 10 (0.9%) | 2 (0.9%) | 1.04 [0.22, 9.79]c |
SBP (mmHg) | 116.3 (±10.5) | 117.0 (±9.2) | − 0.7 [−2.1, 0.7]d |
DBP (mmHg) | 76.6 (±8.7) | 78.6 (±8.3) | −2.0 [−3.3, −0.8] d |
MAP (mmHg) | 89.8 (±8.5) | 91.4 (±7.5) | −1.6 [−2.7, −0.5] d |
CI= confidence interval. DBP= diastolic blood pressure. HTN= hypertension. MAP= mean arterial pressure. SBP=systolic blood pressure.
Values represent n (%) or mean (± standard deviation).
Effect size represents prevalence ratio estimated with log-binomial regression.
Effect size represent odds ratio, estimated with exact logistic regression, given rarity of event.
Effect size represents beta (in mmHg) estimated with linear regression.
Adjusted association of wood fuel use with hypertension and blood pressure
Each covariate in Table 1 not included in the propensity model was evaluated for its univariate association with HTN at delivery. Only four variables were significantly related (Table 3); these covariates were cohort (Jharkhand versus Chhattisgarh), history of hypertension, presence of windows, and use of smokeless tobacco. While the proportion of women whose average daily cooking time was in the upper decile was much higher among wood users compared with gas users (17.8% vs. 8.9%, p=0.0008), HTN was not more common among women who cooked longer (14.2% vs. 16.7%, p=0.36). Other obstetric and maternal characteristics considered were not linked with HTN. Notably, there was no difference in the mean propensity score between hypertensive versus normotensive subjects (0.80 vs. 0.83, p=0.1028) nor was there a linear relation between the frequency of HTN and quintiles of propensity score (p=0.1790). Furthermore, of all the covariates included in the propensity score model, only TV ownership was associated with HTN at a significance level of p <0.05.
Table 3.
Women with HTNa n=212 |
Normotensive womena n=1157 |
Unadjusted effect sizeb [95%CI] |
Adjusted effect sizec [95% CI] |
|
---|---|---|---|---|
Wood fuel use | 166 (78.3%) | 968 (83.66%) | 0.75 [0.56, 1.00] | 0.76 [0.49, 1.17] |
Cohortd Jharkhand Chhattisgarh |
87 (41.0%) 125 (59.0%) |
382 (33.0%) 775 (67.0%) |
1.33 [1.04, 1.71] | 1.03 [0.80, 1.33] |
History of hypertension | 12 (5.7%) | 5 (0.4%) | 4.77 [3.42, 6.65] | 4.09 [2.80, 5.98] |
House has windows | 123 (58.0%) | 837 (72.3%) | 0.59 [0.46, 0.75] | 0.64 [0.49, 0.83] |
Use of smokeless tobacco | 35 (16.5%) | 304 (26.3%) | 0.60 [0.43, 0.84] | 0.71 [0.51, 0.99] |
Upper decile of time spent cooking | 30 (14.2%) | 193 (16.7%) | 0.84 [0.59, 1.21] | ---- |
HTN=hypertension (systolic blood pressure > 139 mmHg or diastolic blood pressure > 89 mmHg). CI= confidence interval.
Values represent n(%).
Effect size represents prevalence ratio, estimated by log-binomial regression.
Covariates included in adjusted model include wood fuel use, categorized propensity score, cohort, history of hypertension, house with windows and use of smokeless tobacco.
Chhattisgarh as referent.
The final adjusted model for HTN included the categorized propensity score (as planned) plus cohort, history of hypertension, presence of windows, and use of smokeless tobacco given the association of these four covariates with HTN (Table 3). After adjustment, wood fuel use was not significantly associated with hypertension (adjusted prevalence ratio 0.76 [95% CI 0.49, 1.17]). A history of hypertension continued to confer and increased risk for HTN at delivery (adjusted prevalence ratio of 4.09 [95%CI 2.80, 5.98]). The presence of windows was associated with a reduction in HTN risk (adjusted prevalence ratio of 0.64 [95% CI 0.49, 0.83]) as was use of smokeless tobacco (adjusted prevalence ratio of 0.71 [0.51, 0.99]).
Linear regression models evaluating the relationship between fuel use and blood pressure measures were subsequently adjusted for the covariates identified in the modeling exercise for HTN at delivery. The association of wood fuel use with a small reduction in DBP and MAP (< 5 mmHg) but not SBP at the time of delivery persisted after adjustment (Table 4).
Table 4.
Adjusted effect sizea [95% CI] |
|
---|---|
SBP (mmHg) | −1.79 [−3.93, 0.26] |
DBP (mmHg) | −2.04 [−3.77, −0.31] |
MAP (mmHg) | −1.96 [−3.60, −0.30] |
CI= confidence interval. DBP= diastolic blood pressure. MAP=mean arterial pressure. SBP= systolic blood pressure.
Effect size represents beta in mmHg estimated by linear regression adjusted for cohort, windows, smokeless tobacco, and history of hypertension.
DISCUSSION
Wood users were one-third less likely to have postpartum blood pressures in the hypertensive range compared with women cooking primarily with gas although this difference did not reach statistical significance. Adjusting for a propensity score that accounted for numerous socioeconomic differences between wood and gas users did little to alter the effect size but served to widen the confidence interval. We did observe that wood fuel users had on average lower mean arterial pressure and diastolic blood pressure at delivery compared to women cooking with gas although this effect size was small (< 5 mmHg) and likely not clinically relevant. Of note, the frequency of a chronic hypertension history was similar between the two groups so this difference does not appear to be driven by a difference in underlying chronic hypertension. The direction of our observed results, even if missing statistical significance, underscores that the link between biomass smoke exposure and an increased risk for hypertension reported from nonpregnant populations14–19 may not translate into a similar effect in a pregnant population. Gestational hypertension and preeclampsia are differentially mediated when compared with chronic hypertension. In chronic hypertension, activation of the sympathetic nervous system and the renin-angiotensin-aldoesterone system are implicated in pathogenesis41; whereas the placenta, clearly absent in nonpregnant individuals, plays a critical role in the development of hypertensive complications of pregnancy. Higher circulating levels of anti-angiogenic factors released from the placenta have been found in women who eventually manifest preeclampsia in their pregnancy; the elevation of these factors may result in widespread endothelial dysfunction with maternal hypertension as one possible manifestation.42,43
It remains plausible that biomass smoke might protect against the development of gestational hypertension or preeclampsia. The combustion byproducts of tobacco and biomass fuels are quite similar and cigarette smoking during pregnancy has been consistently associated with a significantly reduced risk for preeclampsia with a pooled OR of 0.51 [95% CI 0.37, 0.63] reported in meta-analysis.44 Using a Swedish birth registry of over 600,000 births, epidemiologists reported that smokers but not snuff users had a reduced risk for preeclampsia, concluding that cigarette combustion byproducts rather than nicotine itself were responsible for the protection.46 In laboratory experiments, placental cells incubated in the presence of cigarette smoke release less soluble fms-like tyrosine kinase and preserve the release of placental growth factor45, results consistent with a pro-angiogenic state and opposite to the increase in anti-angiogenic factors observed in women that develop preeclampsia.47 Levels of circulating angiogenic markers have not been evaluated in a population of pregnant women exposed to biomass cook smoke.
There are limitations of our study design. Our measurements were limited to those obtained postpartum and we recognize that blood pressure can return to antepartum values following delivery; if anything, this likely biases our results towards the null. Furthermore, as this was a secondary analysis of a cohort recruited to evaluate the prevalence of malaria during pregnancy, measures obtained were not optimized for the diagnosis of gestational hypertension or preeclampsia. We did not have access to urine specimens for the measurement of proteinuria or laboratory results to evaluate end organ involvement in the majority of subjects. Blood pressure measurements from antenatal visits were not available for review and measurements during labor not consistently taken or recorded. Taken together, whether the hypertension we observed represents preeclampsia, gestational hypertension, underlying chronic hypertension or some combination of these is not clear. Moreover, despite our best efforts to account for differences between wood and gas users with the propensity score model, residual confounding cannot be excluded. For example, women cooking with wood fuel may live in more rural locations and be subject to less ambient air pollution from traffic sources than those cooking with gas.
Primary household fuel may imperfectly represent exposure to household air pollution. We had information on only a few variables related to cooking activity. We lacked information on the location of the kitchen (inside versus outside), other fuels used, or other sources of smoke such as trash burning, incense, mosquito coils, and kerosene lamps. Ambient air pollution levels were not available for this cohort. These unexamined factors contribute to a woman’s cumulative exposure to household air pollution and are unlikely reflected in our dichotomous exposure variable (self-reported wood fuel use versus gas use). Interestingly, the presence of windows, which may represent improved indoor ventilation, was significantly associated with a reduction in HTN prevalence in the adjusted model. The finding underscores that further work is required to understand whether an association of cooking smoke and HTN in pregnancy exists and in what direction the effect lies. Study designs that include repeated measurements of personal exposure to air pollutants during such as carbon monoxide and fine particulate matter would improve our ability to classify exposure.
Our analysis is hypothesis-generating, highlighting the need to clarify whether an association between hypertensive disorders of pregnancy and cooking smoke exists. There is growing international momentum among advocacy organizations and governments to promote reductions in household air pollution from cooking with biomass fuels (www.cleancookstoves.org/the-alliance). Several randomized improved stove trials are underway that specifically target pregnant women (Nepal Clinicaltrials.gov #NCT00786877, Ghana clinicaltrials.gov #NCT01335490). Researchers should enumerate what return on investment is to be expected for not only infant but also maternal outcomes. Particular attention should be paid to evaluating whether reductions in cook smoke translate into an altered risk for HTN in pregnancy as policymakers will want to know whether reductions in household air pollution during pregnancy will benefit the mother as well as the infant.
ACKNOWLEDGMENTS
We would like to thank Dr. MK Das, the study nurses, Mobassir Hussain, Amrit Alok, Dr. Meghna Desai, and Dr. V Udhayakumar for their efforts on behalf of the study. We acknowledge the kind administrative and logistical support of the Chief Medical Officers at the participating facilities, the Jharkhand and Chhattisgarh State health officials, and the Indian Council of Medical Research. The United States Agency for International Development (USAID)/India mission provided funding for this study to the Child and Family Applied Research project at Boston University, Boston, MA by means of the USAID cooperative agreement (GHS-A-00-03-00020-00). This work was also supported by the Indo-U.S. Collaborative Network with funding from the Indian Council for Medical Research (ICMR) and the National Institute of Child Health and Development (1 R03 HD52167-01). BJW was supported by the National Institute of Environmental Health Sciences (NIH K23 ES021471). BC was supported by the National Institutes of Health (NIH ES 000002).
Contributor Information
Mrigendra P. Singh, Email: mrigendrapal@gmail.com.
Brent A. Coull, Email: bcoull@hsph.harvard.edu.
Ashlinn Quinn, Email: akq3@columbia.edu.
Kojo Yeboah-Antwi, Email: kyantwi@bu.edu.
Lora Sabin, Email: lsabin@bu.edu.
Davidson H. Hamer, Email: dhamer@bu.edu.
Neeru Singh, Email: oicmrc@yahoo.co.in.
William B. MacLeod, Email: wmacleod@bu.edu.
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