Using 2016 household survey data from Tanzania, we define and measure resilience within the context of Population, Health, and Environment programming and quantify the link between resilience and family planning. We created a multicomponent model using confirmatory factor analysis in a structural equation modeling context. Factor loadings for eight defined latent factors of resilience were statistically significant (p < 0.001). We created a factor called “FP-MCH” reflecting awareness, attitudes, and access to family planning (FP) and health care services and use of maternal and child health care (MCH) facilities. Analysis, with controls, shows that a 1 standard deviation (SD) increase in FP/MCH was associated with a 0.68 SD increase in resilience (p < 0.01), suggesting that the association between FP/MCH and resilience is robust across a range of factors. Analyses showed that the association between FP/MCH is broadly related to the construct of resilience and not through any single component. This study supports the importance of including FP/MCH as part of integrated projects to enhance resilience.
Interest in enhancing the resilience of individuals, households, and communities to contend with climate change-induced and other shocks and stressors in lower- and middle-income countries is growing (Mancini and Bowen 2009; Field et al. 2014; Meyers and Hardee 2017), as is interest in measuring resilience (Quinlan 2014). Resilience has a range of definitions and operates at different scales, but it is generally understood as the ability of an individual, household, community, or system to cope with shocks and stressors, which can be environmental, by responding in ways that maintain their essential functions while expanding their capacity to adapt to change (Folke et al. 2010; Field et al. 2014; UNISDR 2007; Walker et al. 2004). Social and ecological resilience are distinct, but closely linked in literature, particularly in rural areas where communities are reliant upon natural resources for their livelihoods (Adger 2000; Folke et al. 2010).
There is a growing literature on what resilience looks like in practice. In social systems, networks between friends and family, community organization members, and citizens and institutions help build resilience (Adger 2000; Aldrich and Meyer 2014). Resilient ecological systems contain a diversity of flora and fauna that can adapt to environmental changes (Adger 2000; Gunderson 2000). In social–ecological systems, resilience-building practices include adaptive governance (Karpouzoglou et al. 2016), ecosystem management (Virapongse et al. 2016), and disaster risk management (Collier et al. 2009). When social and ecological systems are resilient, they can more readily recover from environmental change and shocks, avoid recurring crises, and develop sustainably (Adger 2000).
Increased attention to the concept of resilience has inspired research into how to best build people’s resilience and ascertain which factors contribute to enhancing resilience. Existing frameworks of resilience have largely ignored the role of population dynamics and the potential for family planning and better reproductive health care to contribute to resilience (Malone 2009; Bremner et al. 2015; Bietsch et al. 2016; Meyers and Hardee 2017; Sathar et al. 2018). However, one exception is USAID’s Program Guidance for Resilience, which states that meeting the unmet need for family planning may be a necessary part of a larger strategy to build resilience (USAID 2012). Furthermore, family planning has been mentioned as a key component in reaching sustainable development goals (Starbird et al. 2016) and as a factor that works on multiple levels to shift people’s ability to adapt to crises, including environmental and climate changes (Smith and Woodward 2014; Husain et al. 2016; Bremner et al. 2015).
While research indicates that integrating family planning and improved reproductive health care into sectors known to contribute to resilience, such as natural resources management, livelihoods, food security, nutrition, and water resources, could further increase that resilience (De Souza 2014; Crist et al. 2017; Naik and Smith 2015; Smith and Smith 2015; Patterson 2018), establishing and measuring the pathways through which resilience is enhanced and the links, if any, among various sectors, is a challenge (Berkes et al. 2003). Currently, the two main links between resilience and family planning and improved reproductive health care found in the literature are (1) the positive effects of the ability to space and plan births on the health of mothers and children (Kock and Prost 2017) and (2) the association between fertility and environmental change. The former fits within the wider link between health and resilience, which posits that good health at the population and individual level are important for short-term response to and long-term recovery from disturbance (NBSB 2014), and that healthy individuals are better able to physically and psychologically withstand events like natural disasters and emotionally cope with the trauma that accompanies any sort of major disturbance (Werner 1995). For the second link between fertility and environmental change, the evidence is mixed, with some studies showing that reduced fertility is related to environmental change, while others show the opposite (Sasson and Weinreb 2017; Brauner-Otto and Axinn 2017; Seller and Gray 2018). More research is therefore needed to more fully understand the link between family planning, reproductive health care, and resilience (PRB and Worldwatch 2014; Yavinsky et al. 2015; Bietsch et al. 2016; Peterson and Giles 2016; Garenne 2017; Grace 2017).
Community-based development projects that simultaneously address livelihoods, natural resources management and conservation, primary health, and reproductive health―commonly known as Population, Health, and Environment or PHE projects―provide an opportunity to study how to measure multiple dimensions of social and environmental resilience and their links with family planning and reproductive health care (Robson et al. 2017). A 2015 synthesis of 35 PHE projects recommended that such projects conduct research to determine whether and how PHE and other integrated projects may contribute to building resilience at the household and community level (Yavinsky et al. 2015).
This research is the first effort to do just that. The paper identifies components of resilience that could be measured in PHE and other integrated development projects, and uses data from a PHE project in western Tanzania to measure resilience and better understand the links between resilience and family planning. The research aims to establish which factors contribute to resilience in the project area, with the ultimate goal of understanding how to build potential resilience among people in ecologically rich regions who rely on natural resources for their livelihoods.
Case study description: the Tuungane Project
The Nature Conservancy and Pathfinder International have implemented the Tuungane Project since 2012 in collaboration with the Tanzania National Parks Authority (TANAPA), local government authorities, and rural communities. The project aims to improve the health of people, forests, and fisheries in the Greater Mahale Ecosystem through strengthening local governance, improving access to social services (particularly health services), and promoting more sustainable use of natural resources (TNC n.d.).
The Tuungane Project was selected for this data collection and research because the social and environmental challenges facing the local communities provide a good case study in which to examine resilience, and because relevant questions could be added to the project’s midterm survey. The area is remarkable for its rich biodiversity, including 250 endemic species of fish (Coulter 1994) and more than 90% of Tanzania’s endangered chimpanzees (Piel et al. 2013). The communities in the project are extremely remote and therefore have very limited access to physical and social infrastructure. They are heavily reliant on their surrounding natural resources for nearly all of their needs. Access to major markets is poor due to a lack of roads, and the nearest major market (Kigoma) is 20 to 30 h away by ferryboat, depending on weather conditions on the lake (Hess and Leisher 2011). The few health facilities must serve large numbers of people, yet are often far from communities and severely undersupplied and understaffed.
A baseline assessment found that the under-five mortality rate in Mahale was among the 20 highest in the world (Hess and Leisher 2011). Virtually all (95%) of the households were reliant on farming, yet frequently face drought conditions, which contribute to food security issues. Income from fishing, which is the main source of cash income in the area, is threatened by overfishing, especially in fish breeding areas close to shore. Fishermen also faced resource supply challenges. Fully 80% of fishers said the average catch had declined compared to five years prior. Findings from a 2011 assessment of health facilities showed an urgent need to address the primary health care needs of people living in the villages around Mahale Mountains National Park (Pathfinder 2011). Infrastructure, staffing, and medical supplies were of concern in all facilities; none had running water or electricity. In addition, a number of barriers prevented access to health services: transportation, spousal permission to seek care, availability of staff at health facilities, quality of services, cost of services, and the ability to access necessary health-related commodities (Pathfinder International 2011).
Climate change-induced stress is expected from temperature increase and changes in rainfall patterns: climate change models suggest the average temperature in western Tanzania has been warming at a rate of 0.12 °C per decade since the 1950s, and will increase by 1.3 to 2.2 °C over the next 40 years; precipitation will increase slightly, with more rainfall during the rainy season but less during the dry season (Gray 2010). Rainfall is also projected to be less predictable (Gray 2010; Girvetz et al. 2014). In short, the vulnerability of residents in the Tuungane Project areas is multidimensional, encompassing factors such as poor health and nutrition status, poverty, illiteracy, gender inequality, degraded natural resources and low agricultural productivity, and governance failures―all of which will be exacerbated by changes in the climate.
Using household survey data from the Tuungane Project’s 2016 midterm review, this paper fills two gaps in the literature. First, we provide a new approach to identify and measure the components of resilience relevant for PHE programming within a structural equation model framework. With this we aim to show the possibility of more broadly incorporating the measurement of resilience into surveys associated with PHE and other integrated development programming. Second, we provide new evidence of the association between resilience and family planning combined with the use of maternal and child health care facilities, which has been theorized in the literature as important for policy and programming, but for which there is a dearth of evidence.
Identifying components of resilience relevant for PHE and integrated development programming
To understand better which components contribute to building resilience in the context of PHE programming, we conducted an extensive literature review and interviewed PHE practitioners (Meyers and Hardee 2017; PRB 2016). Based on these reviews and a 2016 expert meeting held in Arusha, Tanzania, we identified a number of broad components of resilience for which questions can be added to quantitative and qualitative surveys conducted as part of PHE projects. We sought to quantify resilience to shocks that households in economically and geographically isolated regions adjacent to protected areas typically face and often have to resolve on their own: health crises (e.g., cholera outbreaks), food insecurity, and natural resources management within the context of climate change. Because this research was linked to the Tuungane Project’s planned 2016 household survey, we focused on indicators of resilience that can be measured at the family or household level. We were interested in how people cope with environmental change. Eight initial components and their hypothesized linkages to resilience in the context of integrated PHE programming were social capital/social cohesion (engagement, participation, trust, and support); natural resources management (protecting and rebuilding resources); livelihoods and food security (multiple income sources, caloric intake, food reserves); water, sanitation, and hygiene (WASH) (public health infrastructure); health (physical ability to respond to a crisis); education (information access and processing); knowledge of and experience with climate change (increasing adaptive capacity); and attitudes toward population growth (perceived population pressure on ecological sustainability and community wellbeing).
Based on the literature, we hypothesized that there would be a positive link between resilience and family planning plus access to reproductive health care.
Survey and sample
Data come from a 2016 cross-sectional survey of 1010 households in 16 villages near the Mahale Mountains National Park in western Tanzania along the coastline of Lake Tanganyika (Hess et al. 2017). The 16 villages formed the survey sample frame, and the sample division over these villages was proportional to the village size (number of households). Tanzanian villages are administratively divided into sub-villages, and for logistical and cost reasons, two sub-villages were selected per village (each village had between three and eight sub-villages). If a village directly bordered Lake Tanganyika, one lake side and one inland sub-village were selected, with the village sample divided over the selected sub-villages proportional to the combined population size of all coastal and inland sub-villages in that village. Complete household lists of the selected sub-villages were drawn up from which households were randomly selected.
For the purpose of this research, a household was defined as a group of people who live together and usually share their food. The average household size was 6.2 people, and 17% of households were female headed. Children under age 15 comprised 52% of the household population in the sample. A majority of household heads (60%) completed primary school or more, while nearly a quarter (22%) of household heads did not have any formal education.
Interviews were conducted using computer-aided personal interviewing (CAPI). The survey instrument included an overall household section and a reproductive health section. The former was answered by one adult household member, preferably the household head, with sufficient knowledge about the household. Nearly half the respondents to this section were male (49%); at the time of the interview, they were 39 years old on average; respondents were the household head (in 60% of the interviews), his or her spouse (31%), a child of the household head (6%), or another household member (3%). The reproductive health section was answered by one female household member between 18 and 49 years old, if present in the household and available. The reproductive health section was completed in 767 households (76% of the sample); respondents were the spouse of the household head (74%), the household head herself (9%), a child of the household head (10%), or another household member (7%). Sometimes, the same respondent answered both sections of the questionnaire. Most of the households without reproductive health section interviews had no eligible female household members (61%). For the remainder, the reasons for not conducting the section interview were not documented. Because refusal rates for the overall interview were very low (1%), it is assumed that refusal was rare and the unavailability of eligible female household members was the primary reason. As much as possible, the interviews were conducted privately to avoid bias, especially the reproductive health section. Enumerators recorded that 95% of these section interviews were not overheard.
Using the components of resilience identified above as a guide, and with all of the components in the analysis relating to those theorized prior to the survey, in this section, we describe the variables used to measure the different components of resilience, as well as variables used to measure family planning. For consistency, we use the headings of the final components of resilience in the model described below. Differences between the theorized and final components are explained below and in the findings section. The modeling was an iterative process in which different variables and components were tested. All examined variables and components that were tested are described in this section; Table 1 provides descriptive statistics for all variables used in this study. Details on coding for all items are shown in Appendix Table 4. The estimation of the components is described below.
Components of resilience
We included two distinct dimensions of social cohesion: participation and trust. To measure the participation dimension of social cohesion (SC-P), five questions were used. Respondents were asked about their perceived influence on village government decisions; whether people in their village have a positive relationship with TANAPA; whether any household member was part of a village organization; whether any member had attended a public meeting about village land-use planning, health issues, lake management, or forest management in the last year; and whether any household member participated in a Beach Management Unit (BMU), a community governance body that manages the local fisheries.
To measure the trust dimension of social cohesion (SC-T), we used three questions about whether people in the respondent’s village can be trusted, whether people in other villages can be trusted, and whether local government can be trusted.
Natural resource protection attitudes
Seven items were used to measure respondents’ attitudes toward natural resource protection (NR), a proxy for natural resources management. Measuring natural resource management practices directly in a household survey can be problematic given the propensity for social desirability bias to become a factor. While differences can exist between people’s attitudes and practices, we expect changes in attitudes to be reflected in changes in practices over time. Respondents were asked whether forests should be conserved, wildlife should be conserved, and the Mahale Mountains National Park should be conserved. Respondents were also asked whether they believe deforestation causes siltation, whether they believe that siltation harms fish, whether the national park provides benefits to the community, and whether they believe that there is sufficient forest close by to meet day-to-day needs.
Food security and livelihoods and assets
Households’ level of food security and their access to livelihoods and assets (FLA) were measured using nine items, grouped into two dimensions. To measure the food security dimension of this construct, respondents were asked whether they can meet their daily needs and whether they had experienced any food shortages in the last 12 months. The World Food Program Food Consumption Score (FCS) was calculated using questions on consumption frequency in the previous week of 15 different food categories, collapsed into eight food groups (WFP 2009). Additionally, households’ dietary diversity was assessed based on the same questions. Households who had consumed food in four or fewer groups were considered to have low dietary diversity.
To measure the livelihoods and assets dimension of this construct, respondents were asked about the number of crops (varieties) they cultivated, the number of livestock animals they kept, and the size of their owned or rented farm or forest land. Respondents were also asked whether their household had the following items: a bed or mattress, an iron, a sofa, a clock, a radio, a television, a mobile phone, a refrigerator, electricity, solar panels, a generator, a bicycle, a boat without an engine, a boat with an engine, a motorcycle, and a car. This information was used to calculate an assets index similar to the DHS Wealth Index (Rutstein and Johnson 2004) by using principal components analysis to create indicator weights, multiplying each standardized indicator (i.e., z-score) with the corresponding weight, and then summing across weighted indicators. Finally, respondents were asked how many sources of income (i.e., all activities providing food or cash income, including pensions/remittances) their household had.
Water, sanitation, and hygiene
To measure a household’s access to safe water, sanitation, and hygiene (WASH), four items were used. To measure whether households have a safe water source during the dry season, two questions were combined: Respondents were asked to provide information about whether they used an improved source of drinking water during the dry season (i.e., water from protected wells, rain water, bottled water, water from a vendor, or water from a tanker truck) and whether they treated their water supply to make it safer to drink. The same question was asked about a safe water source during the wet season. Respondents were asked whether their household regularly uses an improved toilet facility, which was defined as a toilet facility that is not shared and consists of either a pit latrine with a concrete slab or a pour/flush latrine, and were asked to describe their handwashing practices and show their handwashing facilities (if any).
Health behavior, which has been identified as an important factor of resilience (NBSB 2014), was measured through a proxy, adult use of mosquito bed nets. Female respondents of the reproductive health section were asked whether they slept under a mosquito net the night before the interview. Other health variables that were considered as additional proxies for health behavior include general disease prevalence, malaria incidence, and measles immunization for children. However, general disease prevalence did not correlate highly with any other health variable, and neither malaria incidence nor measles immunization for children had enough variation to sufficiently discriminate between groups and therefore could not be used in the analysis. Although our health component may not capture the full importance of health behavior within resilience, we elected to include the above proxy as we did not want our model to imply that health behavior is not important for resilience.
Women’s highest education level
Education has been positively linked with resilience (Van der Land and Hummel 2013; Lutz and Striessnig 2015). As a proxy measure of the level of education of the members in a household, the highest level of education for the most highly educated woman in each household was included in the model (0 = none or less than primary, 1 = some primary, 2 = completed primary, 3 = some secondary, 4 = completed secondary, 5 = higher than secondary). Additionally, we considered including the education level of the household head, the highest education level of any member, and the average education level of all household members. However, because women’s education is closely linked with economic development and family and child wellbeing, the education level of the most highly educated woman in the household was deemed to be more theoretically relevant.
Climate change awareness
Climate change awareness (CC-A) was measured using four items. Respondents were asked whether they had heard of the term “climate change” (mabadiliko tabia nchi in Kiswahili). Respondents were also asked whether they had observed changes in the weather since they were young, whether they believed that climate change would affect their household, and whether they had changed how they work or live because of these observed changes.
Family planning and access to maternal and child health care
The construct family planning and access to maternal and child health care (FP-MCH) was measured using ten questions; the questions about access to health care were included in the reproductive health section of the questionnaire and were mainly intended to measure access to maternal and child care; thus, they were grouped with family planning knowledge and uptake. This factor included both family planning and maternal and child health care because health and development programming commonly integrates these two services. Respondents were asked whether they know what family planning is, whether they approve of using family planning, whether their household had better access to family planning and health care services compared to 5 years ago, and whether they currently used any method of family planning. Unmet need for family planning is a composite indicator and was determined through a series of questions in the reproductive health section, e.g., the desire to avoid pregnancy, the use of contraceptives, marital status, and fecundity. The indicator was calculated following Bradley et al. (2012). Respondents of the reproductive health section also provided information about whether they visited a health care facility and whether they received a home visit from a health care worker in the 12 months prior to the survey. Community health workers visit each household to support general maternal and child health and family planning needs. Finally, respondents were asked about the number of children they had, the spacing between their children’s births, and whether they wished to have more children. In the initial inventory of potential indicator variables, we considered the variable peoples’ perceptions of population increase as problematic as a variable related to resilience in that such perceptions might be related to family planning; however, this variable was eliminated in favor of more direct attention to family planning and access to maternal and child health services.
Finally, we also included a set of control variables. Demographic controls included the sex and age of the household head and the household size. Socioeconomic controls included whether anyone in the household was employed or ran a business, and whether fishing was a source of household income. Also included was whether the household was a “model household,” which is one of the Tuungane project interventions. Model households are volunteer households that receive training around health, hygiene, the environment, and the relationship between these issues, and then serve as peer educators in their community. Finally, whether a household’s village was located in the project’s northern or southern areas was also included as a control variable to capture differences in remoteness, ethnic makeup, and livelihoods of the areas.
We used confirmatory factor analysis (CFA) to measure the hypothesized components of resilience, as well as resilience itself. CFA is a theory-driven analysis of the relationships between observed variables that tests whether the covariance matrix of the observed data matches the covariance matrix of a hypothesized model (Schreiber et al. 2006). Using this approach, it is possible to estimate exogenous latent constructs that are shared by a set of observed variables, which are considered endogenous or determined by the latent construct. In a structural equation modeling framework (SEM), CFA is also called a measurement model. Besides measurement models, SEM also allows the estimation of structural models, which estimate relationships between latent and observed variables using regression. The goal of measurement and structural models in SEM is to minimize the difference between the covariance matrix of the hypothesized model and the actual covariance matrix of the observed data. In addition to allowing us to model the complex relationships hypothesized in our model, SEM also allows us to estimate unbiased coefficients despite potential multicollinearity (see Appendix Table 5 for the correlation matrix). SEM models require sufficient sample size, with a minimum of 10 observations for each estimated parameter (Schreiber et al. 2006). In our most complex model, we estimate 74 parameters. With a sample size of 1010, we have a ratio of observations to parameters of 13.7:1.
We followed a two-step process to develop a comprehensive measure of resilience using CFA. First, we estimated first-order measurement models for each multi-item construct that was hypothesized to be a component of resilience (i.e., social cohesion–participation; natural resource protection attitudes; food security and livelihoods and assets; water, sanitation, and hygiene; and climate change awareness). We repeated the same process to create a measurement model of family planning and access to MCH care. Second, we estimated a second-order measurement model that incorporates the aforementioned first-order measurement models of the components of resilience, as well as three observed variables (i.e., adult use of mosquito bed nets, women’s highest education level, and changed behavior due to climate change).
Once satisfactory measurement models had been fitted, we used SEM to examine the association between resilience and family planning and access to MCH care. We also tested the hypothesized structural model with the inclusion of all covariates. Finally, we examined the direct association between family planning and access to MCH care and each individual component of resilience to assess whether an association with a particular component of resilience is driving the overall relationship.
All measurement and structural models were estimated using Mplus 6.1 (Muthén and Muthén 2012) with maximum likelihood estimation using weighted least squares estimators using a diagonal matrix with robust standard errors and the Satorra–Bentler chi-squared test for model fit. This estimation approach is most appropriate for models that include binary or ordered categorical dependent variables, as well as non-normally distributed continuous data, as is the case in our models (Brown 2006; Savalei 2014). Pairwise deletion was used to address missing data, which uses information from any observation with available data for both variables in a pair to estimate the correlation matrix. While pairwise deletion results in different numbers of observations being used for different parts of a model, this approach maximizes the data available. This approach is adequate when data are missing at random (MAR), that is, when missingness is explained by observed variables (Allison 2001). Given that the vast majority of missingness is related to whether households participated in the reproductive health section, this is a reasonable assumption.
For all measurement and structural models, model fit was evaluated using a combination of three model fit statistics, since each goodness-of-fit statistic operates on different assumptions (Hoyle and Panter 1995). The comparative fit index (CFI; Gentler 1990) ranges from 0 to 1, with 1 indicating a perfectly fitted model. Values of 0.9 or higher signify good model fit (Bollen 1989; Hoyle and Panter 1995). The root mean square error of approximation (RMSEA) was also used in this study, and values below 0.05 are considered evidence of good model fit (Browne and Dudek 1993). Also presented here is the χ2 statistic; a non-significant value indicates good model fit. However, the χ2 statistic is sensitive to sample size and the large sample size of this study renders this statistic largely undiagnostic. Therefore, the χ2 ratio (χ2/df) is also presented, as this adjusts for sample size. Good fit is indicated by a χ2 ratio between 1 and 3 (Arbuckle and Wothke 1999).
Measurement models establishing proposed latent factors
We composed all first-order latent factors, including family planning and access to MCH care, from their underlying indicator variables through an iterative process. The final unadjusted results for the first-order measurement models are presented in Table 2.
Unstandardized factor loadings are presented to show significance. Standardized factor loadings are presented, with the variance of the latent factor set to 1.00, so that factor loadings can be compared. All first-order measurement models fit well, with at least two fit indices indicating good fit; all factor loadings of the observed variables on the hypothesized factors were significant. Three latent factors―social cohesion–trust; water, sanitation, and hygiene; and climate change awareness―are perfectly fitted because these two factors include only three observed variables and use all degrees of freedom, which means that the models are as complex as the covariate matrices that they explain.
The latent factor social cohesion–participation (SC–P) was indicated by respondents’ perception of their influence on village government decisions, their perception of the village’s relationship with TANAPA, membership in a village organization, attendance at public meetings, and participation in a beach management unit (BMU). Membership in a village organization loaded most highly on this factor (β = 0.77, p < 0.0001). The latent factor social cohesion–trust (SC–T) was indicated by respondents’ trust in people in their village, in people in other villages, and in the village government. Trust in people in respondents’ own village loaded most highly on this factor (β = 0.87, p < 0.0001). The latent factor natural resource protection attitudes (NR) was indicated by a respondents’ opinion of whether forests, wildlife, and the national park should be conserved, whether deforestation causes siltation, whether siltation harms fish, and whether the national park provides community benefits. The opinion that wildlife should be conserved loaded most highly on this factor (β = 0.91, p < 0.0001). The variable measuring belief about the presence of sufficient and proximate forest for day-to-day needs was excluded from the final measurement model because of a notably low factor loading and poor model fit.
The latent factor food security and livelihoods and assets (FLA) reflects the physical livelihoods factor of resilience and was indicated by a household’s ability to meet daily needs, the lack of food shortages, the food consumption score (FCS), the number of crops and livestock animals, and an assets index. Having no food shortages loaded most highly on this factor (β = 0.56, p < 0.0001). The two dimensions of this factor were combined into a single latent construct based on the evaluation of measurement model fit, and the need to have at least three variables per factor. Three observed variables were excluded from this model based on very low factor loadings and poor model fit: household dietary diversity, the amount of owned or rented farm or forestland, and number of income sources. The latent factor water, sanitation, and hygiene (WASH) was indicated by a household’s access to a safe water source during the dry season, improved toilet facilities, and the use of water and soap, ash, or sand to wash hands. Improved toilet facilities loaded the highest on this factor (β = 0.54, p < 0.0001). The observed variable measuring access to a safe water source during the wet season was excluded from the final measurement model because of a very low factor loading and poor model fit, and because there was high correlation between access to safe water in the dry and wet seasons.
The latent factor climate change awareness (CC-A) was indicated by whether the respondent had heard of the term “climate change,” had observed changes in the weather, and believed that climate change would negatively impact their household. Having observed changes in the weather loaded the highest on this factor (β = 0.81, p < 0.0001). The observed variable reflecting changed behavior due to observed changes in weather patterns was initially included in this factor. However, due to low factor loadings and poor model fit, it was included as a separate variable in the second-order measurement model.
Finally, the latent factor family planning and access to MCH care (FP-MCH) was indicated by respondents’ knowledge of family planning, approval of the use of family planning, access to family planning and health care services, and their use of a health care facility or home visit services, mainly for maternal and child health services. Knowledge about family planning loaded the highest on this factor (β = 0.67, p < 0.0001). Four observed variables were excluded from the final measurement model due to very low factor loadings and poor model fit: whether respondents had an unmet need for family planning, the number of children respondents have, the time spacing between births, and whether the respondents want to have more children.
All but three of the first-order measurement models were overidentified with degrees of freedom greater than 0. The measurement models for social cohesion–trust; water, sanitation, and hygiene; and climate change awareness were identified with degrees of freedom equal to 0.
Next, we tested our operationalization of resilience as a second-order latent factor (Table 2). All first-order measurement models (i.e., latent factors) are included in the second-order model of resilience and in all structural models below, with the exception of the latent factor social cohesion–trust, which was excluded due to poor model fit. Again, standardized factor loadings are presented, with the variance of the latent factor set to 1.00, to enable a comparison of factor loadings. This second-order measurement model fit well. The CFI, the RMSEA, and the χ2 ratio all indicated good fit of the second-order measurement model, and all factor loadings of the first-order factors and observed variables on the hypothesized second-order factors were significant. We operationalized resilience as a factor indicated by social cohesion–participation; natural resource protection attitudes; food security and livelihoods and assets; water, sanitation, and hygiene; climate change awareness; adult use of mosquito bed nets; women’s highest education level in a household; and reported behavior change due to observed climate change. Social cohesion–participation loaded most highly on resilience (β = 0.82, p < 0.0001). This was followed by natural resource protection attitudes (β = 0.73, p < 0.0001), climate change awareness (β = 0.66, p < 0.0001), and water, sanitation, and hygiene (β = 0.50, p < 0.0001). The factor loadings for the other included factors and observed variables were lower but still significant; the factor loadings for adult use of mosquito bed nets (β = 0.42, p < 0.0001), food security and livelihoods and assets (β = 0.41, p < 0.0001), and observed behavior change due to climate change (β = 0.41, p < 0.0001) were very similar to each other. The lowest factor loading was for women’s education level (β = 0.34, p < 0.0001). Including other specifications of the education variable (see “Measures” section) had very similar outcomes. This model was overidentified with degrees of freedom greater than 0.
Association between resilience and family planning and access to MCH care
SEM analysis was again used to test the hypothesized association between resilience and family planning and access to MCH care. The results of the unadjusted structural model without the inclusion of any covariates are presented in Fig. 1. All factor loadings are standardized, with the variance of the latent factors set to 1.00 to allow comparison across factor loadings. While the factor loadings on resilience differ from the factor loadings presented in the second-order measurement model because of the inclusion of family planning and access to MCH care in the structural model, the relationships reflected are substantively the same. The regression coefficient representing the association between resilience and family planning and access to MCH care is also standardized. This unadjusted model fit well (CFI = 0.902, RMSEA = 0.032, χ2 (df) = 879.077 (428), χ2 ratio = 2.054), and all factor loadings were significant. These results suggest that a 1 SD increase in family planning and access to MCH care was associated with a 0.67 SD increase in resilience (p < 0.01). This positive association is large and significant.
Figure 2 shows results from the adjusted structural model, which controlled for the sex and age of the household head, whether anyone in the household was employed or ran a business, whether fishing was a source of household income, whether the household was a model household, and the location of the village. While the inclusion of these covariates reduced the fit of this model slightly, two of the fit indices still indicated a good fit (CFI = 0.861, RMSEA = 0.032, χ2 (df) = 1198.084 (597), χ2 ratio = 2.007) and all factor loadings were significant. Moreover, the inclusion of these covariates did not significantly alter the association between resilience and family planning and access to MCH care. Specifically, the adjusted model results show that a 1 SD increase in family planning and access to MCH care was associated with a 0.68 SD increase in resilience (p < 0.01). This suggests that the association between resilience and family planning and access to MCH care is robust across a range of individual, household, and village factors.
Finally, it is important to note that being a “model household” was associated with higher levels of social cohesion–participation (β = 0.17, p < 0.001); water, sanitation, and hygiene (β = 0.11, p < 0.05); and family planning and access to MCH care (β = 0.23, p < 0.001). Similarly, being a female-headed household was associated with lower levels of social cohesion–participation (β = − 0.18, p < 0.01); natural resource protection attitudes (β = − 0.05, p < 0.05); food security and livelihoods and assets (β = − 0.23, p < 0.001); and climate change awareness (β = 0.19, p < 0.001). Appendix Table 6 provides the coefficients for all covariates in each of the first-order measurement models. All structural models were overidentified.
Association between factors of resilience and family planning and access to MCH care
Finally, in order to examine whether the association between family planning and access to MCH care and resilience is driven largely by an association with a specific component of resilience, we also used SEM to estimate the direct associations between the components of resilience and family planning and access to MCH care. The results of these simultaneous regressions are presented in Table 3, in which regression coefficients are standardized. The model, which included all control variables, fit well (CFI = 0.866, RMSEA = 0.032, χ2 (df) = 1149.524 (569), χ2 ratio = 2.020). The results show that family planning and access to MCH care was significantly associated with all components of resilience except food security and livelihoods and assets. However, family planning and access to MCH care was most significantly associated with social cohesion–participation. Specifically, a 1 SD increase in family planning and access to MCH care was associated with a 0.60 SD increase in social cohesion–participation (p < 0.01). Family planning and access to MCH care was also strongly associated with climate change awareness (β = 0.42, p < 0.01), natural resource protection attitudes (β = 0.41, p < 0.01), and adult use of mosquito bed nets (β = 0.40, p < 0.01). Though the associations were lower, family planning and access to MCH care was also significantly associated with water, sanitation, and hygiene (β = 0.33, p < 0.01); observed behavior change due to climate (β = 0.29, p < 0.01); and women’s education level (β = 0.22, p < 0.01).
Alternative specification of family planning
In order to test whether the association between resilience and family planning and MCH care remains robust with the exclusion of MCH care access, we replicated the estimated path model with an alternative specification of the family planning factor that does not include access to MCH care. The alternative family planning factor was indicated by respondent’s knowledge of family planning (β = 0.57, p < 0.0001), approval of the use of family planning (β = 0.49, p < 0.0001), and whether respondents have an unmet family planning need (β = − 0.58, p < 0.0001). The factor is perfectly fitted because it includes only three observed variables (CFI = 1.000, RMSEA = 0.000, χ2 (df) = 0.000 (0)). We then used SEM to test the hypothesized association between resilience and family planning. The results from the adjusted structural model, which included all control variables specified above, show that a 1 SD increase in family planning was associated with a 0.71 SD increase in resilience (p < 0.01) (CFI = 0.865, RMSEA = 0.032, χ2 (df) = 1090.614 (528), χ2 ratio = 2.066). This suggests that the association between resilience and family planning is not solely driven by the inclusion of MCH care access.
This paper presents results of a first-of-its-kind effort to define and measure resilience within the context of PHE multisectoral programming and identify and quantify the link between resilience and family planning combined with use of maternal and child health facilities. The analysis, using data from a 2016 survey in the Tuungane Project in western Tanzania, confirms that resilience can be measured in PHE and other integrated community-based development programming. These measures of resilience can help direct programming. This paper provides evidence that family planning with access to MCH care is positively associated with resilience, a link that had been posited previously but lacked sufficient quantitative evidence.
Based on the literature on resilience and interviews with PHE practitioners, questions related to broad components of resilience were included in the 2016 survey. Among a number of indicators that were hypothesized to comprise resilience, the following multi-item components of resilience emerged: social cohesion–participation; natural resource protection attitudes; food security and livelihoods and assets; water, sanitation, and hygiene; and climate change awareness. We added an additional three observed variables to the model of resilience: adult use of mosquito bed nets (as a proxy for health behavior), women’s highest education level (as a proxy for education), and changed behavior due to climate change (as an added dimension of climate change). The strength of these factor loadings reflects the relative importance of each of these components to the core construct of resilience. All factor loadings were significant; among these, social cohesion–participation had the highest factor loading on resilience, followed by natural resource protection attitudes, climate change awareness, and water, sanitation, and hygiene. This finding makes theoretical sense given that the literature on resilience highlights the primacy of social capital in dealing with adverse weather events, the need for natural resources as a means of rebounding from negative environmental change, and the need for maintaining public health and access to clean water (Meyers and Hardee 2017). While adjustments were made based on available variables from the dataset and on model fit, seven of the eight original components of resilience identified in the literature and in the expert consultation conducted to inform the 2016 survey fit in the final model.
After including family planning/access to MCH care in the model, all factor loadings remained significant, and a positive and strong association between resilience and family planning/access to MCH care was found, both before and after the inclusion of a range of control variables. Moreover, results using an alternative specification of family planning that excludes the maternal and child health care component of this factor confirms that the association between resilience and family planning/access to MCH care is not driven by the inclusion of health care access measures. Thus, there is a strong and significant association between resilience and family planning alone.
The results also show that there is an association between family planning/access to MCH care and the individual components of resilience, with the exception of food security and livelihoods and assets. These results suggest the association between family planning and access to MCH care and resilience is not driven by an association with only one or two specific components of resilience. That food security and livelihoods and assets were not significantly associated with family planning/access to MCH care was surprising and needs more exploration, given the strong theoretical link between food availability and number of mouths to feed in a family (Bremner 2012; Smith and Smith 2015; Borwankar and Amieva 2015).We hypothesize that the theoretical family planning and food security/nutrition links are not reflected in our data because our family planning factor does not reflect reduced fertility, which is an important driver in these theoretical pathways, and we did not measure all food security and nutritional aspects (e.g., stunting). Another possible reason for the lack of association could be temporal: that family planning and access to MCH care is significantly associated with future, but not concurrent, food security and livelihoods and assets. Additional research is necessary to further explore the temporal variations in the relationships between all components of resilience and family planning/access to MCH care. Attention to better measurement of food security and livelihoods and assets is also warranted.
This study had some limitations. Because it was the first of its kind, the components used to define resilience may not be complete. Furthermore, the questions asked in the survey about the components of resilience were not always satisfactory to measure the constructs in the model. For example, we had to use mosquito bed net use as a proxy for health behavior because other questions asked about health behavior did not perform well in the analysis, including questions about general disease prevalence, malaria incidence, and measles immunization for children. We decided to keep the bed net measure in the model because health is a recognized component of resilience (NBSB, 2014), and we did not want our model to imply that health is not important for resilience. Future surveys should include a wider range of questions on health behavior. We also suggest further work on measuring food security and livelihoods and assets. Additionally, because two of the latent constructs in the final model are measured using only three observed variables, it is possible that these factors are too perfectly reflective of the unique variation and relationships reflected in this particular dataset and that the results of these models may not generalize to other populations. Therefore, it is possible that the associations between resilience and family planning and access to maternal and child health care and, indeed, the nature of resilience may differ in other samples. For that reason, replication of these measures with other data sources and their further refinement is a necessary step for future research.
It is also possible that, because the majority of missing data is due to households not having an eligible respondent for the reproductive health section, the results are biased because of the selectivity of the reproductive health section sample. Only households with eligible respondents who were available provided information for several variables in the model that come from this section (e.g., adult use of mosquito bed nets, use of family planning, and visits to a health facility). These households had a younger head of household and had more children than households that did not participate in the reproductive health section. The women in these households are also more educated on average. Therefore, because our model estimation relies more heavily on these younger and more educated households for the associations and covariances of several family planning variables and for mosquito net use, it is possible that we overestimate the role of education and mosquito net use in resilience and, thus, their association with family planning and maternal health care. Finally, a limitation of SEM models is that they do not allow for causal inference, and the association between family planning and access to maternal and child health care and resilience can reflect a relationship that goes in either direction. Therefore, additional research on the directionality of this relationship is needed.
Given the complexity of the models, there was insufficient power to conduct sub-analyses of the findings by group (e.g., female vs. male heads of household), which would show whether the components of resilience have a different configuration for different sub-groups and whether the association between resilience and family planning and access to MCH care varies among different groups. However, by controlling for a set of demographic, socioeconomic, and other household variables, it was possible to assess which characteristics are likely associated with differential levels in each of the components of resilience. Being a “model household” was associated with higher values on family planning and access to MCH care; social cohesion–participation; and water, sanitation, and hygiene. This suggests that the Tuungane Project’s model households are reflecting the desired behavior changes. Yet, the association between resilience and family planning and access to MCH care is significant for all households, including those that did not receive specific training on health, hygiene, and the environment. Additionally, being a female-headed household was associated with lower values of social cohesion–participation, natural resource protection attitudes, food security and livelihoods and assets, and climate change awareness, which suggests that female-headed households are likely less resilient on average than male-headed households. Together, these results are suggestive of sub-group differences in resilience; further research is warranted to investigate the extent of these differences. Additional analysis of other demographic factors, including length of time in the village, migration history, and marital status, would be beneficial.
Moreover, this study has only used indicators of resilience that were collected at household level. While some of these in part also reflect community properties, such as the indicators included in the social cohesion component, our measure of resilience cannot fully capture all its facets, as vulnerability to shocks and changes is determined at multiple levels and varies according to local community characteristics or even the quality of national governance. It would be hard for PHE projects to measure resilience at all these levels, but testing how resilience is measured at the household level could be combined with community-level indicators to create a more encompassing measurement of resilience and would be an interesting addition to the research presented here.
Finally, in factor analysis, certain variables are excluded if they do not fit together well in a single factor. Therefore, our constructs do not include all the data collected in the survey. For example, in food security/nutrition, we created two indicators showing partially conflicting results: (1) a food consumption score showing the households overall had good nutritional values and (2) diet diversity indicating a generally low diet diversity in the study area. Only the former of these indicators fit well within the food security and livelihoods and assets factor, and therefore, the factor does not reflect the full nutritional picture of the area because of the required conditions for factor analysis. Thus, the constructs are sometimes narrower than their factor titles might suggest, and when interpreting the results, it is important to keep in mind which variables comprise each factor. We have listed all variables that were looked at in the analysis in Table 2 since some that did not fit the data from the Tuungane survey might perform better with data from other settings.
Acknowledging these limitations, this study represents a start in the identification of resilience indicators that can be incorporated into the project design and measured within PHE projects as well as other integrated multisectoral development projects to measure resilience, with adaptations for particular project settings. The study also provides evidence of the importance of including family planning and access to maternal and child health care among the components of programming to strengthen resilience. Measuring these indicators over time can help assess whether social resilience is increasing in project areas. This information can be analyzed in conjunction with data on natural resources management and climate change, including gradual change and sudden shocks. In addition, this analysis can inform the design and implementation of holistic programs to strengthen resilience. This analysis can also inform the design and implementation of integrated multisectoral programs to strengthen resilience, helping communities meet multiple development needs―including reproductive health―and cope with climate and environmental shocks.
Adger, W. N. (2000). Social and ecological resilience: are they related? Progress in Human Geography, 24(3), 347–364.
Aldrich, D.P. & Meyer, M.A. (2014). Social capital and community resilience. The American Behavioral Scientist, 59.
Allison, P.D. (2001). Missing data. SAGE Publications.
Arbuckle, J.L. & Wothke, W. (1999). Amos users’ guide, version 4.0. SmallWaters Corporation.
Berkes, F., Kolding, J., & Fowke, C. (2003). Navigating social-ecological systems. Building resilience for complexity and change. Cambridge: Cambridge University Press.
Bietsch, K., Naik, R., Patterson, K.P., Honzak, C., Kudrati, M., Magige, H., Margoluis, C., Subramanian, L., Hale, C., Lamere, C., Hess, S., & Leisher, C. (2016). Analyzing the building blocks of resilience: findings from a baseline survey of the Tuungane population, health, and environment project in Western Tanzania, Working Paper. Washington, DC: Population Council, the Evidence Project. http://evidenceproject.popcouncil.org/wp-content/uploads/2016/11/Tuungane-Research-Report_Nov.-2016.pdf. Accessed December 14, 2016.
Bollen, K. A. (1989). Structural equations with latent variables. New York, NY: Wiley.
Borwankar, R., & Amieva, S. (2015). Desk review of programs integrating family planning with food security and nutrition. Washington, DC: FHI 360/FANTA.
Bradley, S.E.K., Croft, T.N., Fishel, J.D., & Westoff, C.F. (2012). Revising unmet need for family planning. DHS Analytical Studies No. 25. Calverton, Maryland, USA: ICF International. Available at https://dhsprogram.com/publications/publication-as25-analytical-studies.cfm. Accessed September 10, 2018
Brauner-Otto, S. R., & Axinn, W. G. (2017). Natural resource collection and desired family size: a longitudinal test of environment-population theories. Popul Environ, 38, 381–406.
Bremner, J. (2012). Population and food security: Africa’s challenge. Policy Brief. Washington, DC: Population Reference Bureau. http://www.prb.org/pdf12/population-food-security-africa.pdf. Accessed December 28, 2017.
Bremner, J., Patterson, K.P., & Yavinsky, R. (2015). Building resilience through family planning: a transformative approach for women, families and communities. Policy Brief. Washington, DC: Population Reference Bureau. http://www.prb.org/pdf15/sahel-resilience-brief.pdf. Accessed December 14, 2016.
Brown, T. (2006). Confirmatory factor analysis for applied research. New York: Guildford.
Browne, M., & Dudek, R. (1993). Alternative ways of assessing model fit. In K. A. Bolin & J. Long (Eds.), Testing structural equation models (pp. 136–162). Newbury Park, CA: SAGE Publications.
Collier, W. M., Jacobs, K. R., Saxena, A., Baker-Gallegos, J., Carroll, M., & Yohe, G. W. (2009). Strengthening socio-ecological resilience through disaster risk reduction and climate change adaptation: identifying gaps in an uncertain world. Environmental Hazards, 8(3), 171–186.
Coulter, G.W. (1994). Lake Tanganyika. In: Speciation in ancient lakes. Edited by Martens, K., Goddeeris, B. and coulter, G Archiv fur Hydrobiologie 44: 13–18.
Crist, E., Mora, C., & Engelman, R. (2017). The interaction of human population, food production, and biodiversity protection. Science, 356, 260–264.
De Souza, R.M. (2014). Resilience, integrated development and family planning: building long-term solutions, Reproductive Health Matters, 22(43), 75–83.
Field CB, Barros VR, Dokken DJ, Mach KJ, Mastrandrea MD, Bilir TE, Chatterjee M, Ebi KL, Estrada YO, Genova RC, Girma B, Kissel ES, Levy AN, MacCracken S, Mastrandrea PR, & White LL (eds.). (2014). Summaries, frequently asked questions, and cross-chapter boxes. In: Climate change 2014: impacts, adaptation, and vulnerability. A contribution of working group II to the fifth assessment report of the Intergovernmental Panel on Climate Change. Intergovernmental Panel on Climate Change.
Folke, C., Carpenter, S. R., Walker, B., Scheffer, M., Chapin, T., & Rockström, J. (2010). Resilience thinking: integrating resilience, adaptability and transformability. Ecology and Society, 15(4), 20.
Garenne, M. (2017). Crises and resilience in Madagascar: relationships with demographic and social dynamics. In: Wilson-Flores O. Economic crises risk factors, management practices and social impacts. Hauppauge: Nova science Publishers. Pp. 245–264. (Economic Issues, Problems and Perspectives). ISBN 978-1-5361-0357-1.
Gentler, P. M. (1990). Comparative fit indexes in structural models. Psychological Bulletin, 107(2), 238–246.
Girvetz, E. H., Gray, E., Tear, T. H., & Brown, M. A. (2014). Bridging climate science to adaptation action in data sparse Tanzania. Environ Conserv, 41(2), 229–238.
Grace, K. (2017). Considering climate in studies of fertility and reproductive health in poor countries. Nature Climate Change, 7, 479–485.
Gray, E. (2010). Climate change forecasts for Western Tanzania: projected changes in temperature and precipitation over the next 50 and 100 years (Vol. 1). Nature Conservancy: Arlington, VA.
Gunderson, L. H. (2000). Ecological resilience—in theory and application. Annu Rev Ecol Syst, 425–439.
Hess, S. and Leisher, C. (2011). Baseline study for the Tuungane Health and Conservation project. Report. The Nature Conservancy, Arlington, VA, USA: 79 pp. URL: https://www.conservationgateway.org/Documents/Tuungane%20Baseline%20Report.pdf
Hess, S., Leisher, C., Limbu, P., Magige, H., & Kahwa, A. (2017). Changes in household well-being and resilience 2011–2016. Kigoma Region, Tanzania: Tuungane Project.
Hoyle, R. H., & Panter, A. T. (1995). Writing about structural equation models. In R. H. Hoyle (Ed.), Structural equation modeling: concepts, issues, and application (pp. 158–176). Thousand Oaks, CA: SAGE Publications.
Husain, I., Patierno, K., Zosa-Feranil, I., & Smith, R. (2016). Fostering economic growth, equity, and resilience in sub-Saharan Africa: the role of family planning. Washington, DC: PACE Project, PRB http://www.prb.org/pdf16/pace10.16-report-Fostering-Economic-Growth-Equity.pdf. Accessed December 14, 2016.
Karpouzoglou, T., Dewulf, A., & Clark, J. (2016). Advancing adaptive governance of social-ecological systems through theoretical multiplicity. Environmental Science & Policy, 57, 1–9.
Kock, L., & Prost, A. (2017). Family planning and the Samburu: a qualitative study exploring the thoughts of men on a population health and environment programme in rural Kenya. Int J Environ Res Public Health, 14(528), 16. https://doi.org/10.3390/ijerph14050528.
Lutz, W., & Striessnig, E. (2015). Demographic aspects of climate change mitigation and adaptation. Population Studies, 69(S1), S69–S76. https://doi.org/10.1080/00324728.2014.969929.
Malone, EL. (2009). Vulnerability and resilience in the face of climate change: current research and needs for population information. Working Paper PNWD-4087. Richland, WA: Battelle Pacific Northwest Division. http://pai.org/wp-content/uploads/2009/08/Malone_resilience.pdf. Accessed September 10, 2018.
Mancini, JA., & Bowen, GL. (2009). Community resilience: A social organization theory of action and change. Pathways of human development: Explorations of Change, 245–265.
Meyers, A.K. & Hardee, K. (2017). Resilience and community response to climate-related events case studies from four countries, Working Paper. Washington, DC: Population Council, The Evidence Project. http://evidenceproject.popcouncil.org/wp-content/uploads/2017/12/Climate-Resilience-Case-Studies_Working-Paper.pdf. Accessed December 28, 2017.
Muthén, L. K., & Muthén, B. O. (2012). Mplus user’s guide. CA: Los Angeles.
Naik, R., & Smith, R. (2015). Impacts of family planning on nutrition. Washington, DC: Futures Group, Health Policy Project https://www.healthpolicyproject.com/pubs/690_FPandnutritionFinal.pdf. Accessed December 28, 2017.
National Biodefense Science Board (NBSB). (2014). National Biodefense Science Board community health resilience report, 1–13. https://www.phe.gov/Preparedness/legal/boards/nprsb/meetings/Documents/nbsb-chrreport.pdf. Accessed December14, 2017.
Pathfinder International. (2011) Assessment of health facilities and health-seeking behavior in the Greater Mahale Valley: The Tuungane project. https://www.pathfinder.org/wp-content/uploads/2017/08/Assessment-of-Health-Facilities-Health-Seeking-Behavior-in-Mahale.pdf. Accessed September 11, 2018.
Patterson, K. P. (2018). Changes in household well being and resilience: the role of population, family planning and reproductive health in the Tuungane project, synopsis. Washington, DC: Population Council, The Evidence Project http://evidenceproject.popcouncil.org/wp-content/uploads/2018/04/Changes-in-Household-Well-Being-and-Resilience_Synopsis-Brief_March-2018.pdf. Accessed September 14, 2018.
Peterson, R. S., & Giles, M. J. (2016). Children of Tanzania: culturally specific resilience and vulnerability. In B. K. Nastasi & A. P. Borja (Eds.), International handbook of psychological well-being in children and adolescents: bridging the gaps between theory, research, and practice (pp. 221–246). New York: Springer ISBN 978-1-4939-2832-3.
Piel, A. K., Stewart, F. A., Pintea, L., Li, Y., Ramirez, M. A., Loy, D. E., et al. (2013). The Malagarasi River does not form an absolute barrier to chimpanzee movement in western Tanzania. PLoS One, 8(3), e58965.
Population Reference Bureau. (2016). Unpublished notes from an Evidence Project meeting on data exchange regarding resilience. Arusha, Tanzania. February 15–17.
Population Reference Bureau and Worldwatch. (2014). Making the connection: population dynamics and climate compatible development recommendations from an expert working group. Washington DC: PRB and Worldwatch. http://www.prb.org/pdf15/population-climate-full-paper.pdf. Accessed December 14, 2016.
Quinlan, A. (2014). Should we measure resilience? Resilience Science. http://rs.resalliance.org/2014/06/16/should-we-measure-resilience/. Accessed September 10, 2018.
Robson, L., Holston, M., Savitzky, C., & Mohan, V. (2017). Integrating community-based family planning services with local marine conservation initiatives in Southwest Madagascar: changes in contraceptive use and fertility. Studies in Family Planning, 48(1), 73–82.
Rutstein, S. O., & Johnson, K. (2004). The DHS wealth index. DHS comparative reports no. 6. Calverton, MD: Measure DHS+.
Sasson, I., & Weinreb, A. (2017). Land cover change and fertility in West-Central Africa: rural livelihoods and the vicious circle model. Popul Environ, 38, 345–368. https://doi.org/10.1007/s11111-017-0279-x.
Sathar, Z. A., Khalil, M., Hussain, S., Sadiq, M., & Khan, K. (2018). Climate change, resilience, and population dynamics in Pakistan: a case study of the 2010 floods in Mianwali District. Pakistan: Population Council.
Savalei, V. (2014). Understanding robust corrections in structural equation modeling. Struct Equ Model Multidiscip J, 21(1), 149–160.
Schreiber, J., Stage, F. K., Barlow, E., & King, J. (2006). Reporting structural equation modeling and confirmatory factor analysis results: a review. The Journal of Educational Research, 99(6), 323–338.
Seller, S., & Gray, C. (2018). Effects of climate shocks on human fertility in Indonesia: a retrospective, panel analysis of household survey and climate data. The Lancet Planetary Health, 2(Suppl 1), S12.
Smith, E., & Smith, R. (2015). Impacts of family planning on food security. Washington, DC: Futures Group, Health Policy Project.
Smith, K.R., & Woodward, A. [Coordinating Lead Authors]. (2014). Human health: impacts, adaptation, and co-benefits, in ed. Field CB et al. (eds). Climate change 2014: impacts, adaptation, and vulnerability. Part A: global and sectoral aspects. Contribution of working group II to the fifth assessment report of the Intergovernmental Panel on Climate Change Cambridge: Cambridge University Press.
Starbird, E., Norton, M., & Marcus, R. (2016). “Investing in Family Planning: Key to Achieving the Sustainable Development Goals.” Global Health: Science and Practice, 4(2), 191–210.
The Nature Conservancy (TNC). (n.d.). Tanzania. Tuungane Project. Available at http://www.nature.org/ourinitiatives/regions/africa/wherewework/tuungane-project.xml. Accessed September 23, 2017.
United Nations Office for Risk Reduction Management UNISDR. (2007). Resilience. https://www.unisdr.org/we/inform/terminology. Accessed December 12, 2016.
United States Agency for International Development USAID. (2012). Building resilience to recurrent crisis: USAID policy and program guidance. Washington, DC: USAID.
Van der Land, V., & Hummel, D. (2013). Vulnerability and the role of education in environmentally induced migration in Mali and Senegal. Ecology and Society, 18(4), 14. https://doi.org/10.5751/ES-05830-180414.
Virapongse, A., Brooks, S., Metcalf, E. C., Zedalis, M., Gosz, J., Kliskey, A., & Alessa, L. (2016). A social-ecological systems approach for environmental management. J Environ Manag, 187, 83–91.
Walker, B. H., Holling, C. S., Carpenter, S. R., & Kinzig, A. (2004). Resilience, adaptability and transformability in social–ecological systems. Ecology and Society, 9(2), 5 [online] URL: http://www.ecologyandsociety.org/vol9/iss2/art5.
Werner, E. E. (1995). Resilience in development. Current Directions in Psychological Science, 4(3), 81–85.
World Food Program (WFP). (2009). Comprehensive food security & vulnerability analysis guidelines. Rome, Italy: World Food Program Retrieved from http://documents.wfp.org/stellent/groups/public/documents/manual_guide_proced/wfp203208.pdf.
Yavinsky, R.W, Lamere, C., Patterson, K.P., & Bremner. J. (2015). The impact of population, health, and environment projects: a synthesis of evidence, Working Paper. Washington, DC: Population Council, The Evidence Project. http://evidenceproject.popcouncil.org/wp-content/uploads/2015/06/PHE-Synthesis-Report1.pdf. Accessed December 14, 2016.
We thank the people and village leaders in the project area for their participation and facilitation, respectively, in the household surveys, as well as the survey field team. We also thank the participants of an expert meeting in Arusha, Tanzania, in 2016 and current and former colleagues at all of our institutions who provided valuable input and feedback.
The contents of this manuscript are the sole responsibility of the Evidence Project (Population Council and Population Reference Bureau) and the Tuungane Project (The Nature Conservancy and Pathfinder International) and do not necessarily reflect the views of USAID or the United States Government.
Funding for this paper comes from the Evidence and Tuungane Projects. The Evidence Project is made possible by the generous support of the American people through USAID under the terms of cooperative agreement no. AID-OAA-A-13-00087. The Tuungane Project acknowledges the generosity of USAID and the private donors and foundations who have supported the project.
About this article
Cite this article
Hardee, K., Patterson, K.P., Schenck-Fontaine, A. et al. Family planning and resilience: associations found in a Population, Health, and Environment (PHE) project in Western Tanzania. Popul Environ 40, 204–238 (2018). https://doi.org/10.1007/s11111-018-0310-x
- Family Planning
- Climate change