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Health effects of climate change and mitigating effects of climate policies: Evidence from Bangladesh

Eskander, Shaikh,Mahmud, Minhaj Uddin

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Eskander, Shaikh; Mahmud, Minhaj Uddin Working Paper Health effects of climate change and mitigating effects of climate policies: Evidence from Bangladesh ADB Economics Working Paper Series, No. 756 Provided in Cooperation with: Asian Development Bank (ADB), Manila Suggested Citation: Eskander, Shaikh; Mahmud, Minhaj Uddin (2024) : Health effects of climate change and mitigating effects of climate policies: Evidence from Bangladesh, ADB Economics Working Paper Series, No. 756, Asian Development Bank (ADB), Manila, https://doi.org/10.22617/WPS240569-2 This Version is available at: https://hdl.handle.net/10419/310392 Standard-Nutzungsbedingungen: Die Dokumente auf EconStor dürfen zu eigenen wissenschaftlichen Zwecken und zum Privatgebrauch gespeichert und kopiert werden. Sie dürfen die Dokumente nicht für öffentliche oder kommerzielle Zwecke vervielfältigen, öffentlich ausstellen, öffentlich zugänglich machen, vertreiben oder anderweitig nutzen. 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If the documents have been made available under an Open Content Licence (especially Creative Commons Licences), you may exercise further usage rights as specified in the indicated licence. https://creativecommons.org/licenses/by/3.0/igo/ ASIAN DEVELOPMENT BANK ASIAN DEVELOPMENT BANK 6 ADB Avenue, Mandaluyong City 1550 Metro Manila, Philippines www.adb.org ADB ECONOMICS WORKING PAPER SERIES NO. 756 December 2024 Health Effects of Climate Change and Mitigating Effects of Climate Policies Evidence from Bangladesh This paper explores the mitigating effects of climate policies in addressing climate-induced health adversities. It investigates the effect of in utero exposure to rainfall variations on child health in Bangladesh, finding negative effects on children’s anthropometric outcomes. It exploits the heterogeneity in location and timing of district-level allocations for climate projects under the Bangladesh Climate Change Trust Fund to identify that some of these rainfall-induced health adversities can be mitigated through climate policies. About the Asian Development Bank ADB is committed to achieving a prosperous, inclusive, resilient, and sustainable Asia and the Pacific, while sustaining its efforts to eradicate extreme poverty. Established in 1966, it is owned by 69 members —49 from the region. Its main instruments for helping its developing member countries are policy dialogue, loans, equity investments, guarantees, grants, and technical assistance. HEALTH EFFECTS OF CLIMATE CHANGE AND MITIGATING EFFECTS OF CLIMATE POLICIES EVIDENCE FROM BANGLADESH Shaikh Eskander and Minhaj Mahmud ASIAN DEVELOPMENT BANK The ADB Economics Working Paper Series presents research in progress to elicit comments and encourage debate on development issues in Asia and the Pacific. The views expressed are those of the authors and do not necessarily reflect the views and policies of ADB or its Board of Governors or the governments they represent. ADB Economics Working Paper Series Shaikh Eskander and Minhaj Mahmud No. 756 | December 2024 Shaikh Eskander ([email protected]) is an assistant professor at the School of Public Health, University of Alabama Birmingham and a visiting fellow at the Grantham Research Institute on Climate Change and the Environment, London School of Economics and Political Science. Minhaj Mahmud (mmahmud@ adb.org) is a senior economist at the Economic Research and Development Impact Department, Asian Development Bank. Health Effects of Climate Change and Mitigating Effects of Climate Policies: Evidence from Bangladesh Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) © 2024 Asian Development Bank 6 ADB Avenue, Mandaluyong City, 1550 Metro Manila, Philippines Tel +63 2 8632 4444; Fax +63 2 8636 2444 www.adb.org Some rights reserved. Published in 2024. ISSN 2313-6537 (print), 2313-6545 (PDF) Publication Stock No. WPS240569-2 DOI: http://dx.doi.org/10.22617/WPS240569-2 The views expressed in this publication are those of the authors and do not necessarily reflect the views and policies ofthe Asian Development Bank (ADB) or its Board of Governors or the governments they represent. ADB does not guarantee the accuracy of the data included in this publication and accepts no responsibility for any consequence of their use. The mention of specific companies or products of manufacturers does not imply that they are endorsed or recommended by ADB in preference to others of a similar nature that are not mentioned. By making any designation of or reference to a particular territory or geographic area inthis document, ADB does not intend to make any judgments as to the legal or other status of any territory or area. This publication is available under the Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) https://creativecommons.org/licenses/by/3.0/igo/. By using the content of this publication, you agree to be bound bytheterms of this license. For attribution, translations, adaptations, and permissions, please read the provisions andterms of use at https://www.adb.org/terms-use#openaccess. This CC license does not apply to non-ADB copyright materials in this publication. If the material is attributed toanother source, please contact the copyright owner or publisher of that source for permission to reproduce it. ADB cannot be held liable for any claims that arise as a result of your use of the material. Please contact [email protected] if you have questions or comments with respect to content, or if you wish toobtain copyright permission for your intended use that does not fall within these terms, or for permission to use theADB logo. Corrigenda to ADB publications may be found at http://www.adb.org/publications/corrigenda. Note: In this publication, ADB recognizes “Korea” as the Republic of Korea. ABSTRACT This paper explores the mitigating effects of climate policies in addressing climate-induced health adversities. We first investigate the effect of in utero exposure to rainfall variations on child health outcomes in Bangladesh and find that in utero exposure to rainfall variations negatively affects children’s anthropometric outcomes. We then exploit the heterogeneity in location and timing of district-level allocations for climate projects under the Bangladesh Climate Change Trust Fund to identify that some of these rainfall-induced health adversities can be mitigated through climate policies. Our findings are robust to alternative empirical specifications and have important policy implications. Keywords: climate change, climate finance, health, rainfall JEL codes: Q54, Q58, I38 ________________________ We gratefully acknowledge excellent research assistance from Mustafa Kamal and helpful comments and suggestions by the participants of ADB Economists Forum 2023 and Asian Economic Development Conference 2024. 1. Introduction There is growing evidence suggesting that climate change and extreme weather events have detrimental effects on human health, lives, and livelihoods. Extreme temperature, sea-level rise, salinity, floods, storms, and droughts are some of the most common climate change-induced events (Frumkin et al. 2008, Patz et al. 2000). Available literature suggests that some climate events have a direct impact on healthcare infrastructure and thus indirect consequences on individual health. For example, several empirical papers have found extreme temperatures to predict mortality (Curriero et al. 2002; Hajat et al. 2006; Goldberg et al. 2011; Son et al. 2016; Rodrigues, Santana, and Rocha 2019) and hospitalization (Bobb et al. 2014; Schwartz, Samet, and Patz 2004; Son, Bell, and Lee 2014). The 2020 Lancet Countdown report (Watts et al. 2020) concludes that the health impacts of climate change are worsening over time with further deteriorating climate, and countries and populations with heterogenous attributes experience those impacts disproportionately. Similarly, climate events may reduce food production and hamper food distribution to have the same detrimental effects on people’s health. A systematic review of the evidence of health effects of droughts by Stanke et al. (2013), for example, reveals that droughts as a consequence of climate change can lead to adverse indirect health outcomes such as malnutrition and infectious disease. A recent study identified, inter alia, that there can be long-term sustained effects of climate extremes on the affected children including lower health status during adulthood (Eskander and Barbier 2022). While the literature documenting the health effects of climate change has been growing, rigorous empirical evidence focusing on the most vulnerable countries such as Bangladesh is still very limited. Furthermore, the existing research based on secondary, high-frequency data is limited to a few developed economies since the data required for such research is available for only these countries. For example, a recent study by Guimbeau et al. (2024) focused on ocean salinity and its impact on child anthropometric measures in Bangladesh. Mullins and White (2020) found that community health centers in the United States have been successful in reducing the heat-related mortality (but not cold) by 14.2%. More recently, Nyqvist et al. (2023) showed that in Uganda, access to community healthcare centers reduced infant mortality amid adverse weather shocks. However, there is a lack of evidence on mitigating the effects of climate actions to reduce health vulnerability in such a context, which remains a lacuna for policies.1 1 Sustainable Development Goal 13 “Climate Action” emphasizes the need to strengthen resilience and adaptive capacity to climate-related extreme events. 2 In this paper, we consider the potential mitigating effects of climate finance on health adversities arising from frequent disaster exposures such as rainfall variations in the context of Bangladesh. Using three rounds of the household survey data from Bangladesh, we empirically estimate the childhood health effects of in utero exposure to rainfall variations and the mitigating effects of climate policy on these rainfall-induced health adversities. Our results first inform that in utero exposure to rainfall variations significantly reduces exposed children’s anthropometric outcomes, especially their height-for-age (stunting) and weight-for-age (underweight) z scores. We then identify that climate financing projects related to adaptation and mitigation have some mitigating effects on such adversities, by improving children’s anthropometric outcomes. Especially for developing economies like Bangladesh, these findings are very important since both the public and private sectors face repeated budget crises during and after a disaster and our findings, therefore, could at least be generalized to countries experiencing similar situations and impacts. While the climate risks are universal, the tradeoff that a developing economy like Bangladesh faces requires additional attention as these harmful effects of climate change and disasters are further heightened in such a context (Intergovernmental Panel on Climate Change 2012). The scarcity, or often absence, of risk mitigation or insurance programs to protect life, property, and agricultural crops necessitates private coping strategies by the affected households. In such cases, the poorer households set their primary focus on meeting immediate subsistence needs while experiencing frequent climate events, and, therefore, may have to compromise on their preparation for facing such future climatic shocks. Climate policies such as climate legislation, action plans, and financing mechanisms adopted by governments toward risk mitigation and/or adaptation could limit the harmful effects of climate change in such a context. Due to its geographic location and land characteristics, Bangladesh is prone to recurrent flooding and frequent tropical storm events: 26% of the population are affected by cyclones and 70% live in flood-prone regions (Cash et al. 2014). The Bangladesh Climate Change Trust Fund (BCCTF) is a national fund established in 2010 by the Government of Bangladesh to finance climate change activities in the country. It is supported by contributions from the government, international donors, and private sector organizations. The BCCTF is responsible for providing financial resources for a variety of climate change activities in Bangladesh. BCCTF supported projects such as the development of early warning systems for extreme weather events, the promotion of renewable energy sources, and the development of climate-resilient infrastructure. We exploit the heterogeneity in the location and timing of district-level allocations for climate 3 projects under the BCCTF to identify if rainfall-induced health adversities can be mitigated through climate policies. The outline of this paper is as follows: Section 2 describes our data and the empirical strategy and Section 3 reports the results of the health effects of rainfall variations. Section 4 reports the results of the mitigating effects of climate policy. Finally, Section 5 concludes the paper. 2. Data and Empirical Strategy We use three rounds of the Bangladesh Integrated Household Survey (BIHS), 2011–2012, 2015, and 2018–19, for the children’s health outcome variables. BIHS is a nationally representative rural household survey conducted by the International Food Policy Research Institute(IFPRI), details of which can be found in Ahmed (2013). Table 1 provides descriptive statistics. Table 1: Variable Description and Summary Statistics Variables Description Mean SD Minimum Maximum Child’s attributes Males Child’s gender: 1 if male, 0 if female 0.511 0.500 0 1 Age Child’s age in (full) months 29.50 16.84 0 60 Weight Child’s weight in kilogram 10.51 2.941 2.100 23.70 Height Child’s height in centimeter 82.92 13.01 45.10 110 Mother’s attributes Mother’s age Mother’s age in (full) years 27.33 5.835 16 65 Mother’s weight Mother’s weight in kilogram 48.26 9.094 26.90 94.30 Mother’s height Mother’s height in centimeter 150.8 5.686 101.4 195.4 Decision making Indicator of empowerment: 1 if females are involved in food related decisions, 0 if not 0.792 0.406 0 1 Mother’s schooling Schooling indicator: 1 if the mother has some schooling, 0 if not 0.795 0.404 0 1 Household-level attributes Agriculture Proportion of working-age household members working in self-employed agriculture 0.136 0.163 0 0.833 Food insecurity Self-reported measure of extreme poverty: 1 if the household frequently suffers from hunger, 0 if not. 0.0911 0.288 0 1 Child marriage Number of aged 18 or below currently married, widowed, divorced, or separated women in the household 0.0163 0.131 0 2 Regional attributes RWI Relative wealth index, district level measure -0.00453 0.356 -0.963 1.184 Crop diversification Herfindahl–Hirschman index for value of agricultural production, district level measure 0.260 0.0381 0 0.386 Continued on the next page 4 Variables Description Mean SD Minimum Maximum Health outcomes HAZ Length/height-for-age (cm) -1.572 1.430 -10.62 8.301 WAZ Weight-for-age (kg) -1.436 1.123 -8.609 3.566 WHZ Weight-for-length (kg) -0.674 1.233 -12.10 9.057 Climate measures Rainfall variations Deviation of average in utero rainfall from respective long-term average level -3.086 35.48 -92.00 185.2 Rainfall variations T1 Deviation of average first trimester rainfall from respective long-term average level -2.402 54.37 -236.0 404.9 Rainfall variations T2 Deviation of average second trimester rainfall from respective long-term average level -3.349 54.61 -236.3 407.3 Rainfall variations T3 Deviation of average third trimester rainfall from respective long-term average level -3.507 55.19 -185.9 372.3 Flood Frequency of floods in district, 1990-2020: 0 Low (0-5), 1 Medium (6-11) or 2 High (1218) 0: 44.06% 1: 31.45% 2: 24.49% Storm Frequency of storms in district, 1990-2020: 0 Low (0-5), 1 Medium (6-11) or 2 High (1218) 0: 44.06% 1: 39.94% 2: 16.00% Extreme temperature Frequency of extreme temperature events in district, 1990-2020: 0 Low (0-4), 1 Medium (5-8) or 2 High (9-12) 0: 9.82% 1: 72.92% 2: 17.26% Climate policy BCCTF District-level allocation under the BCCTF project, taka per capita 81.37 115.9 0 607.7 CC BCCTF treated cohorts: 1 if the cohort is treated by BCCTF climate funds (i.e., years 2012-18), 0 if not (i.e., years 2007-11) 0.504 0.500 0 1 DD BCCTF treated districts: 1 if the district is treated by BCCTF climate funds, 0 if not 0.850 0.357 0 1 CC2 BCCTF treated child: 1 if the child is in a treated district in treated year (i.e., CC=1 and DD=1), 0 if otherwise 0.208 0.406 0 1 No. of Obs. 6,802 BCCTF = Bangladesh Climate Change Trust Fund, CC = child cohort, CC2 = child cohort 2, DD = district dummy, HAZ = height-for-age z-score, WAZ = weight-for-age z-score, WHZ = weight-for-length z-score. Notes: Summary statistics are for the estimated sample of 6,802 children aged 0–60 months whose mothers were surveyed in any of the three rounds of the Bangladesh Integrated Household Survey (BIHS) data. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). 2.1. Children’s Health Outcomes Among others, the BIHS dataset reports age, birth month, birth year, height, and weight of children aged 0-60 months whose mothers were interviewed during the three survey rounds. Complete data are available for a total of 6,802 children (3,475 males and 3,327 females), who were born between 2007 and 2018, with an average age of 29.50 months, weight of 10.51 kilograms (kg), 11 Following the hypothesis 1, we are interested in the estimated coefficient of 𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖, and we expect that greater (smaller) climate risk (i.e., rainfall variations) decreases (increases) health outcomes, i.e., 𝛼𝛼�1< 0. Hypothesis 2 then refers to the effects of public support aiming at mitigating the harms of climate shock considered in the paper. We focus on the 2010 BCCTF that provides the funding allocations for different climate change-related projects in Bangladesh. We investigate the mitigating effects of BCCTF on climate-induced health adversities described here. For this purpose, we employ the following regression: ℎ𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 =𝛽𝛽0+𝛽𝛽1𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖 +𝛽𝛽2𝑇𝑇𝑖𝑖+𝛽𝛽3𝐹𝐹𝑑𝑑+𝛽𝛽4𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖𝑇𝑇𝑖𝑖+𝛽𝛽5𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖𝐹𝐹𝑑𝑑+𝛽𝛽6𝑇𝑇𝑖𝑖𝐹𝐹𝑑𝑑+𝛽𝛽7𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖𝑇𝑇𝑖𝑖𝐹𝐹𝑑𝑑+𝑋𝑋𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 ′𝛿𝛿+𝜎𝜎𝑖𝑖 +𝜆𝜆𝑖𝑖+𝜌𝜌𝑟𝑟+𝜂𝜂𝑖𝑖𝑖𝑖 +𝜃𝜃𝑖𝑖𝑟𝑟 +𝜑𝜑𝑖𝑖𝑟𝑟 +𝜔𝜔𝑑𝑑 𝑓𝑓+𝜔𝜔𝑑𝑑 𝑠𝑠+𝜔𝜔𝑑𝑑 𝑥𝑥+𝜖𝜖𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖, (2) where ℎ𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖, 𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖, 𝑋𝑋𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 ′ and the set of fixed effects are as defined for equation (1). 𝑇𝑇𝑖𝑖 denotes a staggered measure of climate policy instrument (defined as 1 if child 𝑖𝑖 is treated by climate policy and 0 if not), whereas 𝐹𝐹𝑑𝑑 is a measure of actual allocation of BCCTF funding (defined as the inverse hyperbolic sine transformation of district-level per-capita BCCTF allocation). Therefore,, we are interested in the estimated coefficient of the interaction between 𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖, 𝑇𝑇𝑖𝑖, and 𝐹𝐹𝑑𝑑. Following hypothesis 2, we expect that climate policies reduce climate-induced health adversities so that 𝛽𝛽 󰆹7> 0. The vector of controls 𝑋𝑋𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 ′ includes selected child-, mother-, and household-level attributes that are identified in related literature to have potential confounding effects on the health adversities of rainfall variations and the mitigating effects of climate policies. In all regression specifications, we control for the child’s gender (i.e., 1 if male and 0 if female), age (in full months), and squared age. Mother-level controls include age (in full years), weight (in kg), and height (in cm) of the mother. We also control for household-level prevalence of food insecurity (i.e., 1 if the household has recently encountered an extreme poverty situation such as unavailability of food, 0 if not). We additionally control for regional crop diversity and relative wealth index. Equations (1) and (2) include a series of temporal and spatial fixed effects to control for unobserved heterogeneity that might arise from seasonal and regional variations. In particular, month-of-birth fixed effects account for seasonal variations, whereas monthand year-of-birth fixed effects control for idiosyncratic changes that are common across survey clusters. AEZ fixed effects control for the unobserved time-invariant characteristics specific to the agroecological zone. In addition, AEZ-month fixed effects control for local seasonal variations, AE-year fixed effects control for AEZ-specific annual patterns in health outcomes, and month-year fixed effects 12 control for year-specific seasonal variations. Moreover, flood, storm, and extreme temperature fixed effects control for district-specific heterogeneity in the frequency of disasters. Controlling for above-fixed effects allows us to identify the causal effects of rainfall variations on health outcomes and also the mitigating effects of climate policies on rainfall-induced health adversities (e.g., Dell et al. 2014). Parameter 𝛼𝛼1 in equation (1) allows for differential effects of rainfall on child health outcome and we hypothesize that 𝛼𝛼�1< 0. On the other hand, parameter 𝛽𝛽7 allows for differential effects of climate policies in reducing rainfall-induced child health adversities and we hypothesize that 𝛽𝛽 󰆹7> 0. We assume that 𝑐𝑐𝑐𝑐𝑐𝑐(𝜖𝜖𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖,𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖|ℛ1)= 0 𝑐𝑐𝑐𝑐𝑐𝑐(𝜖𝜖𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖,𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖𝑇𝑇𝑖𝑖𝐹𝐹𝑑𝑑|ℛ2)= 0, (3) where ℛ1 and ℛ2 denote the set of explanatory variables in equations (1) and (2) respectively. Our identifying assumption, therefore, is the independence between the disturbances and the measure of rainfall variations, conditional on permanent differences between the districts of birth and other control variables. This implies that there are no omitted variables that could be correlated with rainfall variations, child health outcomes and climate policies. However, 𝜖𝜖𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 = 𝜂𝜂𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 +𝑢𝑢𝑖𝑖, where 𝑢𝑢𝑖𝑖 is the white noise error term, but 𝜂𝜂𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 may be correlated across 𝑖𝑖 within 𝑑𝑑. We cluster the standard errors at the sub-district or thana level to overcome this problem, which allows for village-level correlations in the error terms. We first adopt an ordinary least squares (OLS) method to estimate equations (1) and (2). However, this is highly likely that rainfall variations are collinear with some of the fixed effects. To address this, we also employ a double-lasso variable selection strategy to select the fixed effects (e.g., Belloni et al. 2014, Guimbeau et al. 2024). This strategy first regresses the variables of interest on the full set of control variables and fixed effects to select a subset of control variables, and then regresses the outcome variable on the variables of interest and selected controls and fixed effects in the second step. The double-lasso strategy is a robust model selection framework that selects a smaller subset of control variables from all potential controls. 3. Health Effects of Rainfall Variations Table 2 reports the health effects of rainfall variations. Panels A and B report OLS and LASSO results, respectively. Overall, all models are statistically significant, and estimated coefficients have expected signs. 13 Table 2: Health Effects of Rainfall Variations (1) (2) (3) (4) (5) (6) A. OLS results B. LASSO results Variables HAZ WAZ WHZ HAZ WAZ WHZ Rainfall variations -0.0022*** -0.0018** -0.0009 -0.0015** -0.0014** -0.0008 (0.0008) (0.0007) (0.0008) (0.0007) (0.0006) (0.0007) Males -0.0438 0.0214 0.0084 -0.0596* 0.0056 -0.0012 (0.0373) (0.0295) (0.0322) (0.0321) (0.0255) (0.0300) Age -0.0913*** -0.0394*** 0.0024 -0.0912*** -0.0372*** 0.0049 (0.0066) (0.0056) (0.0077) (0.0073) (0.0058) (0.0073) Squared age 0.0013*** 0.0004*** -0.0001 0.0013*** 0.0004*** -0.0002 (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) Food insecurity -0.1954*** -0.1800*** -0.0782 -0.2270*** -0.1811*** -0.0541 (0.0576) (0.0508) (0.0567) (0.0552) (0.0443) (0.0510) Mother’s age -0.0043 -0.0082*** -0.0078** -0.0058** -0.0085*** -0.0068*** (0.0038) (0.0027) (0.0030) (0.0030) (0.0023) (0.0026) Mother’s weight 0.0179*** 0.0267*** 0.0227*** 0.0178*** 0.0278*** 0.0245*** (0.0021) (0.0020) (0.0023) (0.0020) (0.0016) (0.0019) Mother’s height 0.0423*** 0.0227*** -0.0050 0.0421*** 0.0221*** -0.0058* (0.0036) (0.0028) (0.0037) (0.0033) (0.0025) (0.0031) Constant -7.4281*** -5.2635*** -0.7633 (0.5501) (0.4003) (0.5233) No. of Obs. 6,760 6,760 6,760 6,802 6,802 6,802 R2 0.2887 0.2860 0.1687 Chi2 680.5*** 830.6*** 190.6*** Birth year FE YES YES YES YES YES YES Birth month FE YES YES YES YES YES YES AEZ FE YES YES YES YES YES YES Birth year × Birth month FE YES YES YES YES YES YES Birth year × AEZ FE YES YES YES YES YES YES Birth month × AEZ FE YES YES YES YES YES YES Flood FE YES YES YES YES YES YES Storm FE YES YES YES YES YES YES Extreme Temperature FE YES YES YES YES YES YES AEZ = agro-ecological zone, FE = Fixed Effects, HAZ = height-for-age z-score, LASSO = least absolute shrinkage and selection Operator, OLS = ordinary least squares, WAZ = weight-for-age z-score, WHZ = weight-for-height z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in column headers. We estimate the health effects of rainfall variations using OLS (columns 1–3) and LASSO (columns 4–6) regressions according to equation (1), where our estimated coefficient of interest is given by the coefficients of the variable “Rainfall variations.” All regressions include the full set of fixed effects and control variables. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). 14 We only focus on the coefficients of LASSO estimates. Column (4) shows that a one-unit increase (decrease) in in utero rainfall variations leads to 0.0015-unit decrease (increase) in HAZ. Similarly, column (5) shows that a one-unit increase (decrease) in in utero rainfall variations leads to 0.0014-unit decrease (increase) in WAZ, while column (6) shows that a one-unit increase (decrease) in in utero rainfall variations leads to 0.0008-unit decrease (increase) in WHZ. We identify significant heterogeneity among male and female children in terms of HAZ: male children have lower HAZ than female children. In general, HAZ and WAZ indices decrease at an increasing rate with age, although the respective age coefficients are statistically insignificant for WHZ. As expected, children from food-insecure households, and those born to older mothers, have lower health status. Mother’s weight has significant and positive effects on all the measures of child health status, whereas the mother’s height affects HAZ and WAZ positively, but WHZ negatively. We also conduct several robustness analyses. Appendix Table A1 also reports the results for binary health outcome variables where we define “stunted” as HAZ<-2, “underweight” as WAZ<-2, and “wasted” as WHZ<-2. Overall, results confirm the presence of health adversities from exposure to rainfall variations and therefore support our main results in Table 2, i.e., rainfall variations increase the probability of stunting by 0.05%, underweight by 0.05%, and wasted by 0.03%. Our results are broadly consistent with results for a specification with trimester rainfall variations. Appendix Table A2 reports the results where we divide total in utero rainfall variations for variations during three trimesters separately. Overall, we identify that HAZ is significantly affected by the second trimester rainfall variations, whereas WAZ is significantly affected by the second and third trimester rainfall variations. Considering the widescale use of irrigation for agriculture in Bangladesh, it is possible that negative rainfall variations may have low or zero adverse effects on agricultural outputs and therefore on health outcomes. Appendix Table A3 reports separate results for drought and flood situations that are defined as negative and positive rainfall variations, i.e., 𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖 < 0 and 𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖 > 0, respectively. As expected, we do not identify any statistically significant health adversities from rainfall variations during the drought situation. However, rainfall variations during flood situations have statistically significant negative effects on health outcomes. Appendix Table A4 reports quantile regression results. While we still observe the significant and negative effect of rainfall variations on HAZ, there are no such adversities for WAZ anymore. 15 Together with our main results and results for flood situations, it is possible that WAZ effects of rainfall variations might be more profoundly felt during heavy floods that create widespread food scarcities. 3.1. Heterogenous Health Effects Table 3 reports the results of the heterogenous impact, where we interacted indicator variables for gender, food insecurity, mother’s health, and population density with rainfall variations to identify respective heterogeneity. Table 3: Heterogenous Health Effects (1) (2) (3) (4) (5) (6) A. Gender B. Food insecurity Variables HAZ WAZ WHZ Variables HAZ WAZ WHZ Rainfall variations -0.0017** -0.0015** -0.0008 Rainfall variations -0.0014* -0.0013** -0.0007 (0.0008) (0.0007) (0.0008) (0.0007) (0.0006) (0.0007) Males -0.0580* 0.0063 -0.0010 Food insecurity -0.2310*** -0.1879*** -0.0599 (0.0321) (0.0255) (0.0300) (0.0554) (0.0454) (0.0520) Rainfall variations × Males 0.0005 0.0002 -0.0000 Rainfall variations × Food insecurity -0.0007 -0.0009 -0.0006 (0.0009) (0.0007) (0.0008) (0.0017) (0.0014) (0.0016) No. of Obs. 6,802 6,802 6,802 No. of Obs. 6,802 6,802 6,802 Set of FEs YES YES YES Set of FEs YES YES YES Controls YES YES YES Controls YES YES YES Chi2 682.7*** 832.0*** 190.7*** Chi2 680.5*** 830.8*** 190.7*** (7) (8) (9) (10) (11) (12) C. Mother's health D. Population density Variables HAZ WAZ WHZ Variables HAZ WAZ WHZ Rainfall variations -0.0009 -0.0020** -0.0018** Rainfall variations -0.0015* -0.0014** -0.0010 (0.0009) (0.0008) (0.0009) (0.0008) (0.0006) (0.0007) Short -0.4663*** -0.2716*** 0.0098 High density 0.1568*** 0.1360*** 0.0522 (0.0454) (0.0367) (0.0442) (0.0494) (0.0408) (0.0465) Rainfall variations × Short -0.0007 0.0006 0.0011 Rainfall variations × High density 0.0013 0.0010 0.0007 (0.0012) (0.0010) (0.0011) (0.0010) (0.0008) (0.0009) Thin -0.3116*** -0.3892*** -0.2746*** (0.0471) (0.0377) (0.0446) Rainfall variations × Thin -0.0003 0.0021** 0.0031*** (0.0012) (0.0010) (0.0012) Short × Thin 0.0124 -0.0106 -0.0274 (0.0655) (0.0526) (0.0624) Rainfall variations × Short × Thin -0.0003 -0.0025* -0.0033** (0.0018) (0.0015) (0.0017) No. of Obs. 6,802 6,802 6,802 No. of Obs. 6,802 6,802 6,802 Set of FEs YES YES YES Set of FEs YES YES YES Controls YES YES YES Controls YES YES YES Chi2 622.4*** 673.3*** 108.5*** Chi2 687.7*** 823.3*** 191.6*** FE = Fixed Effect, HAZ = height-for-age z-score, LASSO = Least Absolute Shrinkage and Selection Operator, WAZ = weight-for-age z-score, WHZ = weight-for-length z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in column headers. We explore the heterogeneity in the health Continued on the next page 16 effects of rainfall variations using LASSO regressions, where we extended equation (1) by introducing additional interaction terms with rainfall variations for each case in Panels A–D which provides our estimated coefficient of interest. All regressions include the full set of fixed effects and control variables. Source: Authors’ calculations using the BIHS dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). Panel A reports heterogeneity impact on gender. While there are significant negative effects of rainfall variations on HAZ and WAZ and male children have significantly lower HAZ, male children having in utero exposure to rainfall variations do not have any significant additional health adversities. Panel B reports the heterogenous impact of the household’s food insecurity status. Like our main results in Table 2, these results confirm that there are significant negative effects of rainfall variations on HAZ and WAZ and food-insecure children have significantly lower HAZ and WAZ. However, we do not identify any exacerbating effects of food insecurity as the estimated coefficients of the interaction term, though negative, are statistically insignificant. Panel C reports the heterogenous impact of the mother’s health. We measure a mother’s health by median height (i.e., 1 if below median height or short, 0 if above median height) and median weight (i.e., 1 if below median weight or thin, 0 if not thin or above median weight). Interestingly, the results show that children born to short mothers have significantly lower HAZ and WAZ, and children born to thin mothers have significantly lower HAZ, WAZ and WHZ. There are no additional adversities from in utero rainfall variations for children of short or thin mothers. However, while children born to short and thin mothers have similar health status, those who experienced in utero rainfall variations and born to short and thin mothers have significantly lower WAZ and WHZ. Panel D reports heterogeneity by district-level population density per square kilometer. It is believed that regions with more facilities are inhabited by more people, and because of their proximity to big urban centers, they also receive disaster and climate risk reduction investments faster. Consistent with this narrative, our results confirm that children born in more densely populated districts have better health status. However, although positive, statistically insignificant coefficients of the interaction term inform that high density does not have any mitigating effects on rainfall-induced health adversities. 17 3.2. Potential Mechanisms of Health Effects Disasters and climate events damage agricultural outputs and therefore create food shortages in affected regions. In utero exposure to such adversities therefore could affect the physical growth and development of exposed children. On the other hand, wealthier regions might have greater adaptive capacity to shocks and therefore may experience lower, if not zero, adversities. To confirm these notions, we consider relative wealth index and crop diversification as potential mechanisms behind rainfall-induced health adversities. Table 4 reports the results where we include relative wealth index and crop diversification as additional controls to see whether the estimated results vary from those in Table 2. Table 4: Health Adversity Mechanisms (1) (2) (3) (4) (5) (6) Wealth Index versification Variables HAZ WAZ WHZ HAZ WAZ WHZ Rainfall variations -0.0016** -0.0014** -0.0008 -0.0015** -0.0013** -0.0008 (0.0007) (0.0006) (0.0007) (0.0007) (0.0006) (0.0007) RWI 0.1787*** 0.1152*** 0.0031 (0.0493) (0.0384) (0.0464) Crop diversification -0.9222 -0.3988 0.1323 (0.5799) (0.4754) (0.5531) Males -0.0592* 0.0057 -0.0009 -0.0598* 0.0060 -0.0024 (0.0321) (0.0256) (0.0301) (0.0320) (0.0255) (0.0300) Age -0.0921*** -0.0379*** 0.0046 -0.0915*** -0.0375*** 0.0047 (0.0073) (0.0058) (0.0073) (0.0072) (0.0058) (0.0072) Squared age 0.0013*** 0.0004*** -0.0001 0.0013*** 0.0004*** -0.0001 (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) Food insecurity -0.2122*** -0.1764*** -0.0597 -0.2136*** -0.1781*** -0.0651 (0.0556) (0.0446) (0.0513) (0.0555) (0.0445) (0.0512) Mother’s age -0.0052* -0.0082*** -0.0069*** -0.0057* -0.0087*** -0.0072*** (0.0030) (0.0023) (0.0026) (0.0030) (0.0023) (0.0026) Mother’s weight 0.0173*** 0.0273*** 0.0242*** 0.0180*** 0.0278*** 0.0244*** (0.0020) (0.0016) (0.0019) (0.0020) (0.0016) (0.0019) Mother’s height 0.0428*** 0.0225*** -0.0057* 0.0422*** 0.0221*** -0.0060* (0.0033) (0.0025) (0.0031) (0.0033) (0.0025) (0.0031) Observations 6,802 6,802 6,802 6,802 6,802 6,802 Chi2 689.4 833.2 186.3 687.9 822.8 187.8 Birth year FE YES YES YES YES YES YES Birth month FE YES YES YES YES YES YES AEZ FE YES YES YES YES YES YES Birth year × Birth month FE YES YES YES YES YES YES Birth year × AEZ FE YES YES YES YES YES YES Birth month × AEZ FE YES YES YES YES YES YES Flood FE YES YES YES YES YES YES Storm FE YES YES YES YES YES YES Extreme Temperature FE YES YES YES YES YES YES Continued on the next page 18 AEZ = agro-ecological Zone, FE = Fixed Effects, HAZ = height-for-age z-score, LASSO = Least Absolute Shrinkage and Selection Operator, RWI = relative wealth index, WAZ = weight-for-age z-score, WHZ = weight-for-length z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in column headers. We explore the role of RWI and crop diversification as transmission mechanisms. Using LASSO regressions, we additionally include these variables in our specification in equation (1). Our estimated coefficient of interest is given by the coefficients of the variable “Rainfall variations.” All regressions include the full set of fixed effects and control variables. Source: Authors’ calculations using the Bangladesh Integrated Household Survey (BIHS) dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). Panel A reports results where we include the relative wealth index as an additional control variable. As expected, children from wealthier regions have statistically significantly higher HAZ and WAZ, and higher but insignificant WHZ. Panel B reports results where we include regional crop diversification, a measure of agricultural diversity, as an additional control variable. Although statistically insignificant, we observe negative relationships of HAZ and WAZ with crop diversification. 3.3. Selection Issues It is possible that the health adversities from exposure to in utero rainfall variations arise from different sources of self-selection bias. For example, male child bias, the prevalence of child marriage, and the mother’s health, entitlement, and education might influence our estimates in Table 2. For this, we collapse data to the thana-birth-year level, calculate measures for these potential sources of selection bias, and then run two-way fixed effect regressions for them on rainfall variations. Table 5: Selection Issues (1) (2) (3) (4) (5) Variables Male bias Selective fertility Entitled mother Educated mother Child marriage Rainfall variations -0.0002 0.0010 -0.0002 0.0001 0.0001 (0.0003) (0.0011) (0.0002) (0.0002) (0.0002) Constant 0.5107*** 2.6488*** 0.8058*** 0.8041*** 0.0433*** (0.0078) (0.0013) (0.0056) (0.0055) (0.0042) No. of Obs. 2,569 2,569 2,569 2,569 2,569 R2 0.1160 0.3971 0.2640 0.3156 0.1729 No. of thana 271 271 271 271 271 Set of FEs NO NO NO NO NO Controls NO NO NO NO NO FE = Fixed Effects, OLS = Ordinary Least Squares. Continued on the next page 19 Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in the column headers. We explore the possibilities of different selection issues by collapsing data to thana-birth-year level, and then running OLS regressions on rainfall variations. We do not include any control variables or fixed effects. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). Table 5 reports the results where we explore these possibilities. First, if there is a bias for male children, our results can be biased since there can be gendered differences in vulnerability to weather extremes (e.g., Arora-Jonsson 2011, Pearse 2017). To check this possibility, we run a regression for the -birth-year level average proportion of male children on average rainfall variations to see whether there is any systematic gender selection in our estimating sample. However, our estimated coefficient, reported in column (1), is statistically insignificant and therefore rules out the possibility of gender selection. Next, women may select their fertility and decide not to give birth during weather and economic adversities. If this is the case, there will be a significantly negative relationship between rainfall variations and incidences of birth. To check this possibility, we collapse data to the thanabirth year level and count the total number of children born in a particular year in each locality. We then use this thana-birth year panel to regress the total number of children born in that year on exposure to rainfall variations. Statistically insignificant results in column (2) confirm that mothers in our estimating sample did not select their fertility decisions. Columns (3) and (4) report results for entitlement (measured by their participation in the household’s food-related decisions) and education (measured by having any schooling) of the mother. It is possible that pregnant women would receive priorities when women are involved in the household’s food-related decisions and when women are educated. If this is the case, then the mother’s entitlement and education should have some mitigating effects on their child’s rainfall-induced health adversities, and we would have to include them in our main specifications as additional controls. To explore these possibilities, we run regressions for thana-birth-year level average entitlement and education of mothers on average rainfall variations. Estimated coefficients are statistically insignificant, and therefore, confirm that mother’s entitlement and education do not necessarily have mitigating effects in our estimating sample. Finally, rainfall variations might affect the incidence of child marriage. The extent of teen pregnancy and other related problems might be greater in regions with greater incidences of child marriage. This might bias our main results since children born to younger mothers may be more 20 vulneable to climate and weather variabilities (e.g., Rylander et al. 2013). To explore this possibility, we collapse data to the thana-birth-year level and count the total number of married women aged below 18 years. We then use this thana-birth-year panel to regress total number of child marriages on rainfall variations. Statistically insignificant results confirm that there is no regional bias arising from excessive incidences of child marriage in our estimating sample. 4. Mitigating Effects of Climate Policy 4.1. Mitigating Effects of Climate Fund We now investigate the mitigating effects of climate policy with regard to health adversities from in utero exposure to rainfall variations according to equation (2). Since we use a staggered treatment for the measure of climate policy, it is important to check for balancing property and parallel trends. First, Appendix Table A5 shows that most of the control variables have significant variations across birth year and birth district. Therefore, it is important to include the components of the vector 𝑋𝑋𝑖𝑖𝑑𝑑𝑖𝑖𝑖𝑖 ′ as controls in all our regressions. Then, Appendix Table A6 shows the results for pre-treatment cohorts and untreated districts. Results for pre-treatment cohorts in Panel A show that the pre-treatment cohorts from treated districts with in utero exposure to rainfall variations have statistically significantly lower HAZ and WAZ. Results are statistically insignificant for untreated districts (Panel B). Together, these results imply that for any causal impact of climate policies in reducing rainfall-induced health adversities, estimated coefficients of interest must be positive and statistically significant. Table 6 reports the mitigating effects of climate policy on health adversities from in utero exposure to rainfall variations for three anthropometry measures according to equation (2). Panels A and B report OLS and LASSO results, respectively. Overall, all models have overall statistical significance, and estimated coefficients exhibit expected directions of relationship with the respective outcome variable. Since results are similar across estimating strategies, we only describe the coefficients from LASSO regressions. We also restrict our discussion to the main coefficients of our interest. 27 Figure A2: Bangladesh Climate Change Trust Fund Allocation BCCTF = Bangladesh Climate Change Trust Fund. Source: Authors’ calculations using the BCCTF dataset. 28 Table A1: Health Effects of Rainfall Variations—Binary Outcome Variables (1) (2) (3) (4) (5) (6) A. OLS results B. LASSO results Variables Stunted Underweight Wasted Stunted Underweight Wasted Rainfall variations 0.0007** 0.0007** 0.0002 0.0005* 0.0005** 0.0003* (0.0003) (0.0003) (0.0002) (0.0003) (0.0002) (0.0002) Males 0.0147 -0.0170 -0.0027 0.0201* -0.0110 -0.0004 (0.0133) (0.0120) (0.0079) (0.0113) (0.0108) (0.0077) Age 0.0184*** 0.0096*** -0.0019 0.0188*** 0.0083*** -0.0020 (0.0022) (0.0023) (0.0020) (0.0023) (0.0023) (0.0018) Squared age -0.0003*** -0.0001*** 0.0000 -0.0003*** -0.0001** 0.0000 (0.0000) (0.0000) (0.0000) (0.0000) (0.0000) (0.0000) Food insecurity 0.0573*** 0.0781*** -0.0003 0.0613*** 0.0714*** 0.0005 (0.0220) (0.0228) (0.0148) (0.0206) (0.0206) (0.0144) Mother’s age 0.0014 0.0020* 0.0005 0.0015 0.0026*** 0.0005 (0.0012) (0.0011) (0.0007) (0.0010) (0.0010) (0.0007) Mother’s weight -0.0059*** -0.0080*** -0.0030*** -0.0058*** -0.0086*** -0.0034*** (0.0008) (0.0008) (0.0005) (0.0007) (0.0007) (0.0005) Mother’s height -0.0130*** -0.0087*** 0.0003 -0.0131*** -0.0083*** 0.0006 (0.0012) (0.0013) (0.0009) (0.0011) (0.0010) (0.0008) Constant 2.3294*** 1.7744*** 0.2414* (0.1872) (0.1737) (0.1314) No. of Obs. 6,760 6,760 6,760 6,802 6,802 6,802 R2 0.2247 0.2093 0.1358 Chi2 491.1*** 501.9*** 75.33*** Set of FEs YES YES YES YES YES YES FE = fixed effects, HAZ = height-for-age z-score, LASSO = Least Absolute Shrinkage and Selection Operator, OLS = ordinary least squares, WAZ = weight-for-age z-score, WHZ = weight-for-height z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in the column headers, where stunted is defined as HAZ<-2, underweight as WAZ<-2, and wasted as WHZ<-2. We estimate the health effects of rainfall variations using OLS (columns 1–3) and LASSO (columns 4–6) regressions according to equation (1), where our estimated coefficient of interest is given by the coefficients of the variable “Rainfall variations”. All regressions include the full set of fixed effects and control variables. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016; IFPRI 2020). 29 Table A2: Health Effects of Trimester Rainfall Variations (1) (2) (3) (4) (5) (6) OLS results LASSO results Variables HAZ WAZ WHZ HAZ WAZ WHZ Rainfall variations T1 -0.0009 -0.0002 0.0003 -0.0000 0.0002 0.0004 (0.0005) (0.0004) (0.0005) (0.0004) (0.0003) (0.0004) Rainfall variations T2 -0.0009* -0.0007* -0.0005 -0.0008* -0.0007** -0.0005 (0.0005) (0.0004) (0.0005) (0.0004) (0.0003) (0.0004) Rainfall variations T3 -0.0005 -0.0009** -0.0007 -0.0006 -0.0008** -0.0005 (0.0005) (0.0004) (0.0005) (0.0004) (0.0003) (0.0004) Males -0.0439 0.0218 0.0090 -0.0529 0.0074 -0.0041 (0.0373) (0.0295) (0.0322) (0.0322) (0.0254) (0.0299) Age -0.0913*** -0.0394*** 0.0024 -0.0891*** -0.0370*** 0.0048 (0.0066) (0.0056) (0.0077) (0.0073) (0.0059) (0.0074) Squared age 0.0013*** 0.0004*** -0.0001 0.0012*** 0.0004*** -0.0001 (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) Food insecurity -0.1949*** -0.1811*** -0.0801 -0.2311*** -0.1849*** -0.0574 (0.0574) (0.0509) (0.0570) (0.0552) (0.0444) (0.0512) Mother’s age -0.0043 -0.0082*** -0.0078** -0.0058* -0.0086*** -0.0070*** (0.0038) (0.0027) (0.0030) (0.0030) (0.0023) (0.0026) Mother’s weight 0.0179*** 0.0267*** 0.0227*** 0.0179*** 0.0276*** 0.0241*** (0.0021) (0.0020) (0.0023) (0.0020) (0.0016) (0.0019) Mother’s height 0.0423*** 0.0227*** -0.0051 0.0421*** 0.0222*** -0.0056* (0.0036) (0.0028) (0.0037) (0.0033) (0.0025) (0.0031) Constant -7.4250*** -5.2569*** -0.7513 (0.5490) (0.4009) (0.5251) No. of Obs. 6,760 6,760 6,760 6,802 6,802 6,802 R2 0.2888 0.2861 0.1691 Chi2 670.5*** 817.8*** 184.8*** Birth year FE YES YES YES YES YES YES Birth month FE YES YES YES YES YES YES AEZ FE YES YES YES YES YES YES Birth year × Birth month FE YES YES YES YES YES YES Birth year × AEZ FE YES YES YES YES YES YES Birth month × AEZ FE YES YES YES YES YES YES Flood FE YES YES YES YES YES YES Storm FE YES YES YES YES YES YES Extreme Temperature FE YES YES YES YES YES YES AEZ = agro-ecological zone, BCCTF = Bangladesh Climate Change Trust Fund, FE = fixed effects, HAZ = height-for-age z-score, IHS = inverse hyperbolic sine, LASSO = least absolute shrinkage and selection operator, OLS = ordinary least squares, WAZ = weight-for-age z-score, WHZ = weight-for-length z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in column headers. We estimate the health effects of rainfall variations using OLS (columns 1–3) and LASSO (columns 4–6) regressions according to equation (1), where our estimated coefficient of interest is given by the coefficients of the variables “Rainfall variations T1”, “Rainfall variations T2” and “Rainfall variations T3”. All regressions include the full set of fixed effects and control variables. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016; IFPRI 2020). 30 Table A3: Health Effects During Drought and Flood Situations (1) (2) (3) (4) (5) (6) Drought situation Flood situation Variables HAZ WAZ WHZ HAZ WAZ WHZ Rainfall variations 0.0011 0.0001 -0.0008 -0.0041*** -0.0017* 0.0011 (0.0016) (0.0013) (0.0015) (0.0012) (0.0010) (0.0011) Males -0.0470 0.0194 0.0057 -0.0734 0.0081 0.0102 (0.0417) (0.0336) (0.0398) (0.0509) (0.0403) (0.0471) Age -0.1004*** -0.0455*** 0.0034 -0.0761*** -0.0250*** 0.0044 (0.0088) (0.0072) (0.0091) (0.0121) (0.0091) (0.0119) Squared age 0.0014*** 0.0005*** -0.0001 0.0010*** 0.0002 -0.0001 (0.0001) (0.0001) (0.0001) (0.0002) (0.0001) (0.0002) Food insecurity -0.1897*** -0.1279** -0.0118 -0.3741*** -0.3568*** -0.1975** (0.0724) (0.0553) (0.0635) (0.0873) (0.0750) (0.0857) Mother’s age -0.0011 -0.0030 -0.0023 -0.0099** -0.0151*** -0.0127*** (0.0039) (0.0031) (0.0035) (0.0047) (0.0035) (0.0040) Mother’s weight 0.0153*** 0.0283*** 0.0271*** 0.0232*** 0.0277*** 0.0199*** (0.0026) (0.0021) (0.0025) (0.0032) (0.0026) (0.0030) Mother’s height 0.0401*** 0.0191*** -0.0091** 0.0474*** 0.0268*** -0.0029 (0.0044) (0.0032) (0.0043) (0.0048) (0.0040) (0.0044) No. of Obs. 4,109 4,109 4,109 2,693 2,693 2,693 Chi2 393.7*** 489.1*** 129.4*** 321.3*** 351.6*** 66.49** Birth year FE YES YES YES YES YES YES Birth month FE YES YES YES YES YES YES AEZ FE YES YES YES YES YES YES Birth year × Birth month FE YES YES YES YES YES YES Birth year × AEZ FE YES YES YES YES YES YES Birth month × AEZ FE YES YES YES YES YES YES Flood FE YES YES YES YES YES YES Storm FE YES YES YES YES YES YES Extreme Temperature FE YES YES YES YES YES YES AEZ = agro-ecological zone, FE = fixed effects, HAZ = height-for-age z-score, IHS = inverse hyperbolic sine, LASSO = least absolute shrinkage and selection operator, OLS = ordinary least squares, WAZ = weight-for-age z-score, WHZ = weight-for-height z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in the column headers. We estimate the health effects of rainfall variations using LASSO regressions according to equation (1) for drought and flood situations that are defined as negative and positive rainfall variations, i.e., 𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖 < 0 and 𝑐𝑐𝑑𝑑𝑖𝑖𝑖𝑖 > 0, respectively. Our estimated coefficient of interest is given by the coefficients of the variable “Rainfall variations”. All regressions include the full set of fixed effects and control variables. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). 31 Table A4: Health Effects of Rainfall Variations: Quantile Regressions (1) (2) (3) Variables HAZ WAZ WHZ Rainfall variations -0.0010** 0.0001 -0.0000 (0.0005) (0.0006) (0.0005) Males 0.0998** 0.0000 0.0690* (0.0418) (0.0519) (0.0359) Age -0.0146*** -0.0204*** -0.0229*** (0.0054) (0.0052) (0.0029) Squared age 0.0001 0.0002*** 0.0002*** (0.0001) (0.0001) (0.0000) Food insecurity -0.0136 0.0138 0.0462 (0.0544) (0.0628) (0.0842) Mother’s age 0.0019 0.0027 -0.0011 (0.0047) (0.0029) (0.0036) Mother’s weight -0.0033 -0.0011 0.0015 (0.0033) (0.0020) (0.0024) Mother’s height 0.0029 0.0044 -0.0001 (0.0046) (0.0028) (0.0036) Constant 1.4330** 0.9430** 1.7823*** (0.6831) (0.4261) (0.5297) No. of Obs. 6,802 6,802 6,802 Set of FEs NO NO NO FE = fixed effects, HAZ = height-for-age z-score, WAZ = weight-for-age z-score, WHZ = weight-for-height z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in the column headers. Quantile regressions follow the specification (1) excluding the fixed effects. Our estimated coefficient of interest is given by the coefficients of the variable “Rainfall variations”. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). 32 Table A5: Balancing Properties (1) (2) (3) (4) (5) (6) (7) CC 0 CC 0 CC 1 CC 1 Variables DD 0 DD 1 DD 0 DD 1 (2) – (1) (3) – (1) (4) – (1) Males 0.526 (0.500) 0.496 (0.500) 0.496 (0.501) 0.525 (0.499) -0.0299 -0.0298 -0.0006 Age 34.25 (16.93) 33.57 (17.20) 25.48 (15.37) 25.37 (15.47) -0.6814 - 8.7756*** -8.8840*** Weight 11.03 (2.901) 10.93 (2.965) 10.07 (2.844) 10.09 (2.869) -0.0922 -0.952*** -0.936*** Height 85.56 (12.78) 84.91 (13.18) 80.89 (12.46) 80.86 (12.59) -0.6495 -4.6717*** -4.6951*** Mother’s age 27.10 (5.941) 27.73 (5.973) 27.33 (5.537) 26.99 (5.707) 0.6328** 0.2304 -0.1047 Mother’s weight 46.76 (8.460) 46.78 (8.490) 49.65 (9.562) 49.72 (9.416) 0.0271 2.8970*** 2.9660*** Mother’s height 150.3 (5.216) 150.6 (5.886) 150.7 (5.608) 151.0 (5.577) 0.3101 0.4348 0.7184*** Decision making 0.687 (0.464) 0.722 (0.448) 0.845 (0.363) 0.871 (0.336) 0.0356* 0.1577*** 0.1838*** Mother’s schooling 0.705 (0.456) 0.732 (0.443) 0.853 (0.355) 0.862 (0.344) 0.0268 0.1478*** 0.1573*** Agriculture 0.201 (0.193) 0.175 (0.178) 0.0841 (0.123) 0.0950 (0.131) -0.0259*** -0.1170*** -0.1060*** Food insecurity 0.101 (0.301) 0.118 (0.323) 0.0714 (0.258) 0.0667 (0.250) 0.0174 -0.0293* -0.0340*** Child marriage 0.00549 (0.0740) 0.00530 (0.0774) 0.0294 (0.181) 0.0268 (0.166) -0.0002 0.0239*** 0.0213*** RWI -0.0382 (0.355) -0.00870 (0.355) -0.0414 (0.370) 0.0116 (0.354) 0.0295* -0.0032 0.0499*** Crop diversification 0.246 (0.0355) 0.261 (0.0377) 0.249 (0.0405) 0.262 (0.0377) 0.0154 0.0034 -0.0161*** HAZ -1.824 (1.386) -1.820 (1.397) -1.394 (1.280) -1.317 (1.443) 0.0043 0.4301*** 0.5065*** WAZ -1.644 (1.100) -1.607 (1.099) -1.320 (1.061) -1.252 (1.128) 0.0377 0.3242 0.3920*** WHZ -0.742 (1.193) -0.679 (1.196) -0.678 (1.119) -0.657 (1.290) 0.0631 0.0644 0.0856 No. of Obs. 546 2,828 476 2,952 BCCTF = Bangladesh Climate Change Trust Fund, HAZ = height-for-age z-score, IHS = inverse hyperbolic sine, OLS = ordinary least squares, RWI = relative wealth index, WAZ = weight-for-age z-score, WHZ = weight-for-height z-score. Notes: Balancing properties are for the estimating sample of 6,802 children aged 0–60 months whose mothers were surveyed in any of the three rounds of the Bangladesh Integrated Household Survey (BIHS) data. CC denotes BCCTF-treated cohorts, i.e., 1 if the cohort is treated by BCCTF climate funds (i.e., years 2012–2018), 0 if not (i.e., years 2007–2011), whereas DD denotes BCCTF treated districts, i.e., 1 if the district is treated by BCCTF climate funds, 0 if not. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI 2016], IFPRI 2020). 33 Table A6: Parallel Trends (1) (2) (3) (4) (5) (6) Pre-treatment cohorts Untreated districts Variables HAZ WAZ WHZ HAZ WAZ WHZ Rainfall variations 0.0019 0.0026 0.0019 0.0019 0.0026 0.0019 (0.0020) (0.0016) (0.0018) (0.0020) (0.0016) (0.0018) Treated districts -0.0237 0.0026 0.0454 (0.0829) (0.0579) (0.0614) Rainfall variations × Treated districts -0.0045** -0.0056*** -0.0029 (0.0022) (0.0018) (0.0020) Treated cohorts 0.4217*** 0.3058*** 0.0491 (0.0870) (0.0650) (0.0615) Rainfall variations × Treated cohorts -0.0038 -0.0010 0.0006 (0.0027) (0.0021) (0.0023) Constant -1.8123*** -1.6283*** -0.7310*** -1.8123*** -1.6283*** -0.7310*** (0.0758) (0.0510) (0.0544) (0.0767) (0.0516) (0.0550) No. of Obs. 3,374 3,374 3,374 1,022 1,022 1,022 R2 0.0026 0.0060 0.0012 0.0274 0.0258 0.0051 Set of FEs NO NO NO NO NO NO Controls NO NO NO NO NO NO FE = fixed effects, HAZ = height-for-age z-score, WAZ = weight-for-age z-score, WHZ = weight-for-height z-score. Notes: Robust standard errors in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in the column headers. The estimated sample is restricted to the untreated households only, therefore providing a test for parallel trend assumption. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016; IFPRI 2020). 34 Table A7: Mitigating Effects of Climate Policies: Binary Outcome Variables (1) (2) (3) (4) (5) (6) OLS results LASSO results Variables Stunted Underweight Wasted Stunted Underweight Wasted Rainfall variations 0.0007 0.0002 -0.0001 0.0005 0.0000 0.0000 (0.0005) (0.0005) (0.0003) (0.0005) (0.0004) (0.0003) Treated children -0.0050 -0.0340 0.0206 -0.0097 0.0019 0.0093 (0.0740) (0.0720) (0.0459) (0.0694) (0.0623) (0.0502) Rainfall variations × Treated children 0.0011 0.0030** 0.0017 0.0014 0.0035** 0.0017 (0.0014) (0.0013) (0.0011) (0.0015) (0.0014) (0.0011) IHS(BCCTF) -0.0058 -0.0060 -0.0022 -0.0044 -0.0044 -0.0017 (0.0051) (0.0041) (0.0028) (0.0040) (0.0039) (0.0026) Rainfall variations × IHS(BCCTF) -0.0000 0.0002 0.0001 0.0000 0.0002* 0.0001 (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) (0.0001) Treated children × IHS(BCCTF) 0.0087 0.0146 0.0006 0.0074 0.0067 0.0018 (0.0160) (0.0139) (0.0094) (0.0139) (0.0125) (0.0099) Rainfall variations × Treated children × IHS(BCCTF) -0.0002 -0.0006** -0.0003 -0.0002 -0.0008*** -0.0003 (0.0003) (0.0003) (0.0002) (0.0003) (0.0003) (0.0002) Males 0.0146 -0.0169 -0.0026 0.0194* -0.0118 -0.0010 (0.0134) (0.0121) (0.0079) (0.0115) (0.0110) (0.0078) Age 0.0184*** 0.0098*** -0.0019 0.0189*** 0.0083*** -0.0021 (0.0022) (0.0023) (0.0020) (0.0023) (0.0023) (0.0018) Squared age -0.0003*** -0.0001*** 0.0000 -0.0003*** -0.0001** 0.0000 (0.0000) (0.0000) (0.0000) (0.0000) (0.0000) (0.0000) Food insecurity 0.0568** 0.0773*** -0.0008 0.0585*** 0.0699*** -0.0030 (0.0220) (0.0227) (0.0148) (0.0208) (0.0209) (0.0143) Mother’s age 0.0015 0.0021* 0.0005 0.0014 0.0023** 0.0007 (0.0012) (0.0011) (0.0007) (0.0010) (0.0010) (0.0007) Mother’s weight -0.0059*** -0.0080*** -0.0030*** -0.0058*** -0.0083*** -0.0034*** (0.0008) (0.0008) (0.0005) (0.0007) (0.0007) (0.0005) Mother’s height -0.0129*** -0.0086*** 0.0003 -0.0131*** -0.0086*** 0.0006 (0.0012) (0.0013) (0.0009) (0.0011) (0.0010) (0.0008) Constant 2.3373*** 1.7869*** 0.2422* (0.1898) (0.1728) (0.1305) No. of Obs. 6,760 6,760 6,760 6,802 6,802 6,802 R2 0.2252 0.2107 0.1367 Chi2 480.7*** 489.5*** 76.05** Set of FEs YES YES YES YES YES YES BCCTF = Bangladesh Climate Change Trust Fund, FE = fixed effects, HAZ = height-for-age z-score, IHS = inverse hyperbolic sine, LASSO = least absolute shrinkage and selection operator, OLS = ordinary least squares, WAZ = weight-for-age z-score, WHZ = weight-for-height z-score. Notes: Robust standard errors clustered at thana level in parentheses. ***, **, and * represent statistical significance at 1-, 5-, and 10-percent levels, respectively. All variables follow their respective definitions in Table 1. Dependent variables are reported in the column headers, where stunted is defined as HAZ<-2, underweight as WAZ<-2, and wasted as WHZ<-2. We estimate the mitigating effects of climate policy on the health effects of rainfall variations using OLS (columns 1–3) and LASSO (columns 4–6) regressions according to equation (2). Our estimated coefficients of interest are given by the coefficients of the interaction term “Rainfall variations × Treated children × IHS(BCCTF)”. All regressions include the full set of fixed effects and control variables. Source: Authors’ calculations using the Bangladesh Integrated Household Survey dataset (Ahmed 2013, International Food Policy Research Institute [IFPRI] 2016, IFPRI 2020). 35 REFERENCES Adélaïde, Lucie, Olivier Chanel, and Mathilde Pascal. 2022. “Health Effects from Heat Waves in France: An Economic Evaluation.” The European Journal of Health Economics, 23 (1): 119–31. Ahmed, Akhter. 2013. “Bangladesh Integrated Household Survey (BIHS) 20112012”, https://doi.org/10.7910/DVN/OR6MHT, Harvard Dataverse, V5. Arora-Jonsson, Seema. 2011. “Virtue and Vulnerability: Discourses on Women, Gender and Climate Change.” Global Environmental Change, 21 (2): 744–51. Auffhammer, M., Hsiang, S.M., Schlenker, W. and Sobel, A. 2013. “Using Weather Data and Climate Model Output in Economic Analyses of Climate Change.” Review of Environmental Economics and Policy, 7 (2): 181–98 Barreca, Alan, Karen Clay, Olivier Deschênes, Michael Greenstone, and Joseph S. Shapiro. 2016. “Adapting to Climate Change: The Remarkable Decline in the US TemperatureMortality Relationship over the Twentieth Century.” Journal of Political Economy, 124 (1): 105–59. Barreca, Alan I. 2012. Climate Change, Humidity, and Mortality in the United States. Journal of Environmental Economics and Management, 63 (1): 19–34. Belloni, Alexandre, Victor Chernozhukov, and Christian Hansen. 2014. “Inference on Treatment Effects After Selection Among High-Dimensional Controls.” The Review of Economic Studies, 81 (2): 608–50. Bobb, Jennifer F., Ziad Obermeyer, Yun Wang, and Francesca Dominici. 2014. “Cause-Specific Risk of Hospital Admission Related to Extreme Heat in Older Adults.” JAMA 312 (24): 2659–67. Cash, Richard A., Shantana R. Halder, Mushtuq Husain, Md Sirajul Islam, Fuad H. Mallick, Maria A. May, Mahmudur Rahman, and M. Aminur Rahman. 2014. “Reducing the Health Effect of Natural Hazards in Bangladesh.” The Lancet, 382 (9910): 2094–103. Chi, Guangha, Han Fang, Sourav Chatterjee, and Joshua E. Blumenstock. 2022. “Micro Estimates of Wealth for All Low-and Middle-Income Countries.” Proceedings of the National Academy of Sciences, 119 (3): p.e2113658119. Cole, TJ., 1989. “Using the LMS Method to Measure Skewness in the NCHS and Dutch National Height Standards.” Ann Hum Biol. 1989 Sep–Oct; 16 (5): 407–19. Curriero, Frank C., Karlyn S. Heiner, Jonathan M. Samet, Scott L. Zeger, Lisa Strug, and Jonathan A. Patz. 2002. “Temperature and Mortality in 11 Cities of the Eastern United States.” American Journal of Epidemiology, 155 (1): 80–87. Das, Debasish Kumar, Md Sariful Islam, Sheikh Hadiujjaman, Champa Bati Dutta, and Md Manjur Morshed. 2019. “Health Cost of Salinity Contamination in Drinking Water: Evidence from Bangladesh.” Environmental Economics and Policy Studies 21 (3): 371– 97. 36 Deschênes, O. and Greenstone, M., 2011. “Climate Change, Mortality, and Adaptation: Evidence from Annual Fluctuations in Weather in the US.” American Economic Journal: Applied Economics, 3 (4): 152–85. Deschênes, Olivier, and Enrico Moretti. 2009. “Extreme Weather Events, Mortality, and Migration.” The Review of Economics and Statistics, 91 (4): 659–81. Deschênes, Olivier, Michael Greenstone, and Jonathan Guryan. 2009. “Climate Change and Birth Weight.” American Economic Review, 99 (2): 211–7. Deschênes, Olivier. 2022. “The Impact of Climate Change on Mortality in the United States: Benefits and Costs of Adaptation.” Canadian Journal of Economics, 55 (3):1227–49. EM-DAT, C.R.E.D. 2020. The OFDA/CRED International Disaster Database. Université Catholique. Eskander, Shaikh M., and Edward B. Barbier. 2022. “Long-Term Impacts of the 1970 Cyclone in Bangladesh.” World Development, 152, 105793. Frumkin, Howard, Jeremy Hess, George Luber, Josephine Malilay, and Michael McGeehin. 2008. “Climate Change: The Public Health Response.” American Journal of Public Health, 98 (3): 435–45. Goldberg, Mark S., Antonio Gasparrini, Ben Armstrong, and Marie-France Valois. 2011. “The Short-Term Influence of Temperature on Daily Mortality in the Temperate Climate of Montreal, Canada.” Environ Res, 111 (6): 853–60. Guimbeau, Amanda, Xinde Ji, Nidhiya Menon, and Zi Long. 2024. “Ocean salinity, early-life health, and adaptation.” Journal of Environmental Economics and Management, 125: 102954. Haines, Andy, and Jonathan A. Patz. 2004. “Health Effects of Climate Change.”. Jama, 291 (1): 99–103. Hajat, Shakoor, Ben Armstrong, Michela Baccini, Annibale Biggeri, Luigi Bisanti, Antonio Russo, Anna Paldy, Bettina Menne, and Tom Kosatsky. 2006. “Impact of High Temperatures on Mortality: Is There an Added Heat Wave Effect?” Epidemiology, 17 (6): 632–8. Hübler, Michael, Gernot Klepper, and Sonja Peterson. 2008. “Costs of Climate Change: The Effects of Rising Temperatures on Health and Productivity in Germany.” Ecological Economics, 68 (1): 381–93. IFPRI. 2016. “Bangladesh Integrated Household Survey (BIHS) 2015.” https://doi.org/10.7910/DVN/BXSYEL, Harvard Dataverse, V4. IFPRI. 2020. “Bangladesh Integrated Household Survey (BIHS) 2018– 2019.” https://doi.org/10.7910/DVN/NXKLZJ, Harvard Dataverse, V2. Intergovernmental Panel on Climate Change. 2012. Summary for Policymakers. In [Field, C.B., V. Barros, T.F. Stocker, D. Qin, D.J. Dokken, K.L. Ebi, M.D. Mastrandrea, K.J. Mach, G.- K. Plattner, S.K. Allen, M. Tignor, and P.M. Midgley (eds.)]. Managing the Risks of