Next Article in Journal
The Impact of the COVID-19 Pandemic on Research and Volunteering Activities among Medical Students: A Cross-Sectional Study among Romanian and International Students from One Medical Faculty from Romania
Next Article in Special Issue
Frequency, Types, and Manifestations of Partner Sexual Violence, Non-Partner Sexual Violence and Sexual Harassment: A Population Study in Spain
Previous Article in Journal
A Transparency Checklist for Carbon Footprint Calculations Applied within a Systematic Review of Virtual Care Interventions
Previous Article in Special Issue
Relationship between Vehicle Safety Ratings and Drivers’ Injury Severity in the Context of Gender Disparity
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
IJERPH
Volume 19
Issue 12
10.3390/ijerph19127476
ijerph-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Decision Tree Analyses to Explore the Relevance of Multiple Sex/Gender Dimensions for the Exposure to Green Spaces: Results from the KORA INGER Study

by
Lisa Dandolo
1,2,*,
Christina Hartig
1,2,
Klaus Telkmann
1,2,
Sophie Horstmann
1,2,
Lars Schwettmann
3,4,
Peter Selsam
5,
Alexandra Schneider
6,†,
Gabriele Bolte
1,2,† and
on behalf of the INGER Study Group
‡
1
Department of Social Epidemiology, Institute of Public Health and Nursing Research, University of Bremen, 28359 Bremen, Germany
2
Health Sciences Bremen, University of Bremen, 28359 Bremen, Germany
3
Institute of Health Economics and Health Care Management, Helmholtz Zentrum München, German Research Center for Environmental Health (GmbH), 85764 Neuherberg, Germany
4
Department of Economics, Martin Luther University Halle-Wittenberg, 06108 Halle (Saale), Germany
5
Department Monitoring and Exploration Technologies, Helmholtz Centre for Environmental Research GmbH—UFZ, 04318 Leipzig, Germany
6
Institute of Epidemiology, Helmholtz Zentrum München, German Research Center for Environmental Health (GmbH), 85764 Neuherberg, Germany
*
Author to whom correspondence should be addressed.
†
These authors contributed equally to this work.
‡
Members as listed below in the Acknowledgments.
Int. J. Environ. Res. Public Health 2022, 19(12), 7476; https://doi.org/10.3390/ijerph19127476
Submission received: 28 April 2022 / Revised: 10 June 2022 / Accepted: 15 June 2022 / Published: 18 June 2022
(This article belongs to the Special Issue Gender Inequalities in Health and Social Determinants)
Browse Figures
Review Reports Versions Notes

Abstract

:
Recently, attention has been drawn to the need to integrate sex/gender more comprehensively into environmental health research. Considering theoretical approaches, we define sex/gender as a multidimensional concept based on intersectionality. However, operationalizing sex/gender through multiple covariates requires the usage of statistical methods that are suitable for handling such complex data. We therefore applied two different decision tree approaches: classification and regression trees (CART) and conditional inference trees (CIT). We explored the relevance of multiple sex/gender covariates for the exposure to green spaces, measured both subjectively and objectively. Data from 3742 participants from the Cooperative Health Research in the Region of Augsburg (KORA) study were analyzed within the INGER (Integrating gender into environmental health research) project. We observed that the participants’ financial situation and discrimination experience was relevant for their access to high quality public green spaces, while the urban/rural context was most relevant for the general greenness in the residential environment. None of the covariates operationalizing the individual sex/gender self-concept were relevant for differences in exposure to green spaces. Results were largely consistent for both CART and CIT. Most importantly we showed that decision tree analyses are useful for exploring the relevance of multiple sex/gender dimensions and their interactions for environmental exposures. Further investigations in larger urban areas with less access to public green spaces and with a study population more heterogeneous with respect to age and social disparities may add more information about the relevance of multiple sex/gender dimensions for the exposure to green spaces.

1. Introduction

Sex/gender with its multiple biological and social dimensions has not yet been adequately considered in environmental health research [1,2,3,4]. To comprehensively assess the impact of gender relations as well as sex-linked biology, there has been a call to integrate sex/gender with its complexity and entanglement of biological and social dimensions into health research beyond a simple binary approach [5,6,7,8]. We use the term “sex/gender” to express this entanglement of sex and gender [9,10]. Moreover, an intersectionality perspective strengthens the consideration of structural causes of health inequities such as systems of power and discrimination processes [11,12].
To meet the challenge of a comprehensive integration of sex/gender into environmental health research, various data to depict multidimensionality, variety, embodiment and intersectionality in the study of sex/gender impacts [9] have to be used in multivariate statistical analyses. In quantitative health research, standard methods to examine relationships between covariates and outcomes are regression models. These are, however, limited to a small number of covariates and are not flexible enough to uncover unspecified, complex, and non-linear covariate-outcome relationships [13,14]. A family of methods to analyze complex and high-dimensional data are decision trees, also called recursive partitioning. Decision trees are exploratory, non-parametric methods that recursively partition a sample into subgroups based on covariate values, thereby classifying individuals into subgroups that are homogeneous with respect to the main outcome [14,15]. Decision trees have also been identified as particularly useful methods for research based on intersectionality theory [16,17,18] as they can identify complex and unsuspected interactions between covariates, even if they are non-linear [16].
Although decision trees are not as widely used as regression models, researchers have been encouraged to use them in epidemiological or public health research [14,15,19]. In recent research, decision trees have therefore been used to identify subgroups with homogeneous health outcomes [17,20,21,22] or health-related behaviors [13,16,18]. Mena [17] for instance, used an intersectional-informed approach to find subgroups that show a high prevalence of frequent mental distress. While Winkler [18] applied decision trees to investigate the involvement in physical activity and sleep in a young adult population.
As an exemplary thematic field for the comprehensive integration of sex/gender into environmental health, we chose exposure to green spaces in the residential environment. Within environmental health research, green spaces and green infrastructure have been proven to be an important environmental resource of health [23,24,25,26]. Green spaces act as places for socialising, exercise and recreation [23,27,28] and can have a positive impact on physical activity as well as social and psychological well-being [29]. Green spaces also reduce exposure to noise, air pollutants and intense heat and improve air quality [25,27,29].
In recent years evidence increased that social inequalities exist in availability of, or access to, green spaces. Evidence suggests that population groups with lower socioeconomic positions have less access to environmental resources like green spaces [30,31,32]. However, sex/gender—as an important social determinant of health—is not often analyzed in studies on social inequalities in exposure to green spaces [31]. A few studies discussed differences in the usage of public green spaces and parks by a binary sex/gender category [33,34,35], without considering sex/gender differences in the exposure to green spaces.
The aim of our study was twofold: firstly, we wanted to test whether decision trees are suitable methods to analyze complex data when integrating multiple sex/gender dimensions into environmental research. Currently there are debates about advantages and disadvantages of different types of decision trees [15,36]. Referring to these, we compared two types of decision trees: the most often used classification and regression trees (CART) [37,38] and a prominent alternative, conditional inference trees (CIT) [39,40]. Secondly, by applying decision tree methods, we aimed to identify and describe homogeneous subgroups with respect to exposure to green spaces, considering a large range of sex/gender covariates simultaneously and their possible interactions.

2. Materials and Methods

2.1. INGER Project

The focus of the collaborative research project INGER (https://www.uni-bremen.de/en/inger, accessed on 25 May 2022) was to integrate sex/gender into environmental health research. The project aimed to develop innovative methods for data collection and analyses in population-based studies on environmental health, to be able to assess the impacts of sex/gender more comprehensively. Within INGER, we developed a multidimensional sex/gender concept with a focus on intersectionality [9] and created new sex/gender questionnaire modules to improve sex/gender data collection in population-based studies. We used this newly developed INGER questionnaire within the Cooperative Health Research in the Region of Augsburg (KORA) study to investigate the aforementioned research questions.

2.2. Study Population

The research platform KORA was designed to evaluate the links between health, disease and the living conditions of the population of Augsburg and two adjacent counties [41]. Since 1984, four cross-sectional surveys at intervals of 5 years and various follow-ups have been conducted. The four surveys were S1 (1984/85, participants born between 1920 and 1959), S2 (1989/90, 1915–1964), S3 (1994/95, 1920–1969) and S4 (1999–2000, 1925–1974). In 2019, the paper-based INGER questionnaire was sent to 5256 eligible KORA participants aged 44–93 years. These participants included all participants of the KORA FIT study, which was conducted in 2018/2019 and to which participants of all four surveys with a current age of 54–75 years were invited. In addition, the INGER questionnaire was sent to all younger participants of S3 (49–53 years) and to all other participants of S4 who had not participated in KORA FIT (44–53 and 74–93 years). Within the INGER survey, participants answered the newly developed sex/gender questionnaire module as well as an extensive set of questions about residential green spaces.

2.3. Sex/Gender Covariates

For our main decision tree analyses we chose a total of 40 sex/gender covariates based on our INGER multidimensional sex/gender concept [9]. This concept describes an individual sex/gender self-concept that is embedded in an environment and society that is defined by structural sex/gender relations. When operationalizing this concept, 17 covariates represent the individual sex/gender self-concept: one covariate each for the dimensions sex assigned at birth and current sex/gender identity, twelve covariates operationalizing the dimension internalized sex/gender roles, and three covariates for the dimension externalized sex/gender expressions. We included 23 covariates that contribute to explain the structural sex/gender relations: nine covariates corresponding to the experience of discrimination, eight covariates related to care activities, and six covariates corresponding to intersectionality-related social categories. For a complete list of the 40 covariates, including the questions asked and possible answer categories for each question see Table 1.
As some variables included in the KORA FIT survey can add some additional information that can be interpreted with respect to our INGER multidimensional sex/gender concept [9], we decided to run additional decision tree analyses for all INGER participants who had also taken part in the KORA FIT study with a total of 53 covariates, i.e., the original 40 covariates plus 13 additional ones. Of the 13 new covariates, six correspond to intersectionality-related social categories, three portray health related behaviors and four covariates are psychosocial factors. For a complete list of the 13 extra covariates, including the questions asked within the KORA FIT survey, as well as the possible answer categories for each question see Supplementary Table S1.

2.4. Exposure Variables

We operationalized green spaces in two different ways. Firstly, we measured the subjectively reported access to public green spaces and the quality of these public green spaces. Secondly, we considered the general greenness in the residential environment, measured both subjectively and objectively. The subjective measurements were based on our KORA INGER survey and the objective measurements comprise Normalized Difference Vegetation Index (NDVI) data available for the participants’ residential address. Overall, we ran decision tree analyses for five different exposure variables.

2.4.1. Access to Public Green Spaces (Subjectively Measured)

Participants were asked whether they had access to public green spaces in their residential environment, naming parks, forests, or meadows as examples (one variable).

2.4.2. Access to High Quality Public Green Spaces (Subjectively Measured)

This exposure measure with three answer categories (access to high quality public greenspaces, access only to lower quality public greenspaces, no access to public green spaces), was based on a combination of three questions: the first question was the one described above about the access to public green spaces. The participants who answered no to this question were classified as having no access to public green spaces. The participants who answered yes to this question were further divided into having access to high quality public green spaces vs. access only to lower quality public green spaces based on their response to two follow-up questions about the quality of available green spaces. In these follow-up questions, participants were asked to indicate on a five-point scale from strongly agree to strongly disagree, whether the green spaces in their residential environment were well maintained, and secondly whether the green spaces in their residential environment were of high quality. We classified participants within the category access to high quality public green spaces when they gave the answer “strongly agree” to both above statements, and all other remaining participants were categorized as having access only to lower quality public green spaces.

2.4.3. Greenness in the Residential Environment (Subjectively Measured)

Participants were asked how green their neighborhood was, considering every type of greenspace, from grass verges on the streets to gardens and parks. The original question had four answer categories (very green, a little green, hardly green, not green at all). The last two categories had a very small sample size (hardly green = 69, not green at all = 9), so these two were grouped together as hardly green.

2.4.4. Greenness within a 300 or 1000 m Buffer around the Residential Address (Objectively Measured)

For these two exposure variables we used NDVI data, calculated for the year 2019. NDVI is a measure of vegetation density, i.e., greenness [42]. We used Landsat 8 Operational Land Imager (OLI) satellite images with a resolution of 30 m and Sentinel-2 images with 10 m ground resolution with less than 1% cloud cover for single images. Image and quality selection as well as all calculations were performed using Google’s Earth Engine Code Editor (https://code.earthengine.google.com, accessed on 4 October 2021). Images were collected during April to October and calculated as median of all accepted images relying on the atmospherically corrected reflectance of near-infrared (NIR) and visible red (RED) light, using the standard formula: NDVI  =  (NIR − RED)/(NIR  +  RED). NDVI values comprise a possible value range from −1 to +1 with values about 0 and lower indicating rock, sand, snow, water and densely urbanized areas, values near +1 a very high density of photosynthetic active plants [43,44]. Negative values were set to NAs (missing values). Water areas were masked according to the Copernicus Global Land Cover Map [45]. For each participant, the NDVI values within a certain buffer around their residential address were averaged. We chose two different buffers, a 300 m, and a 1000 m buffer, the first representing the area one can easily access by foot and the second a more extended area as a direct comparison.

2.5. Recursive Partitioning

Recursive partitioning is a statistical method used for subgroup analysis. A decision tree is grown, which provides a partitioning of the sample population into several subgroups based on dichotomized independent variables. The root node contains the entire sample and is depicted at the top of a tree. A split produces two mutually exclusive subnodes determined by a splitting rule. Each split is induced on a single independent variable and aims to maximize the homogeneity of the target variable within the subgroups. This procedure is carried out recursively at each subnode until some stopping criterion is met. Nodes without successors are called leaves or terminal nodes. Edges resemble decision rules. For more details and applications, we refer to [14,15,19] and references therein. Different algorithms employ different stopping criteria and metrics to measure homogeneity. In this article we focus on two types of recursive partitioning algorithms, namely CART [37] and CIT [39]. A major advantage of both of these decision tree methods compared to e.g., standard regression models is that they have an intrinsic mechanism to handle missing values in the covariates. A complete case analysis is not necessary. In a first step, where the best splitting variable is chosen, observations that have missing values in the currently evaluated covariate are ignored. Observations with missing values are then assigned to child nodes by so-called surrogate splits, which mimic the decision rule as closely as possible [46].

2.6. Classification and Regression Trees (CART)

CART, developed by Breiman [37], refers to two types of decision tree algorithms: classification trees are applied when the target variable is categorical, whereas regression trees cover numerical outcomes.

2.6.1. Splitting Criteria

CART is a greedy algorithm and searches for the best split among all permissible splits. Classification trees measure the homogeneity in a node (or the lack thereof) by misclassification error, information gain or Gini impurity. In contrast, regression trees minimize the variance. In both cases the quality of a split is then determined by averaging these measures for both resulting subnodes. In our analyses, classification trees using Gini impurity are grown to analyze the three subjective exposure measures while regression trees are applied to the NDVI exposure variables.

2.6.2. Stopping Criteria

The algorithm terminates if one of several possible stopping criteria is met. A common rule is to specify a minimum number n m i n of observations in a node. A split is only induced if both resulting child nodes contain at least n m i n observations. This is often set to about 1% of the sample size [19]. However, it has been recommended to use no less than 50 observations as a minimum bound, as terminal nodes with less observations lack statistical robustness and have little predictive power [47]. Therefore, we set the minimum number of observations allowed in a node to 50. This is also comparable to a recent study that had a similar sample size and used the same threshold [22]. Another often used criterion is to bound the depth of the tree, i.e., the maximum number of consecutive splits. In our analyses we restricted the maximal depth of the tree to four.

2.6.3. Pruning

Despite the above-mentioned stopping criteria, tree-based methods are still prone to overfitting. This means that the tree becomes too large such that the derived decision rules are too specific and may not be applicable to other data [14]. Therefore, it is common to prune the tree until only meaningful subgroups are left. Breiman [37] suggests applying cross-validation to select the best subtree. They recommend identifying the tree with the smallest cross-validation error and then adding its corresponding standard error (SE). The smallest tree within this range is said to follow the so-called 1-SE rule and is deemed the best-sized subtree. However, it has recently been shown that this 1-SE rule is rather conservative with quite a low type one error [15]. An alternative, less conservative pruning rule is to choose the subtree corresponding to the minimum cross-validation error [15,16,36,48]. Here, we will present the CART trees based on this less conservative pruning rule, but will also describe whether the more conservative pruning based on the 1-SE rule would have led to the same tree. In rpart one can also set an a-priori complexity parameter (cp) value to avoid CART to grow overly large trees that are then always pruned back in the next step. The default value in rpart is cp = 0.01, but this sometimes leads to over-pruning in larger datasets missing out on meaningful splits [38]. We therefore set the cp value to a less conservative 0.001 and performed pruning as described above.

2.6.4. Variable Importance

CART also calculates a variable importance measure that indicates how important the covariates were in the splitting process. This is performed by considering all occurrences at which the covariate appears, either as a primary or as a surrogate splitting variable. This measure can help to identify variables which are not represented in splits because they are masked by other variables, possibly due to collinearity. The variable importance values across all covariates are scaled to sum up to 100 [38].

2.7. Conditional Inference Trees (CIT)

CIT is a decision tree method developed by Hothorn [39]. The major difference to CART is that feature selection and the actual splitting process are separated. Moreover, it utilizes a concept of statistical significance to determine splitting variables.

2.7.1. Splitting Criteria

To avoid an exhaustive search, a p-value driven feature selection step searches for the best splitting variable. More specifically, in the first step, for each covariate the null-hypothesis of independence of the target variable is tested at some prespecified significance level α. The covariate with the strongest bivariate association with the dependent variable is selected. In a second step, the algorithm identifies the optimal binary partition based on the selected covariate. This two-step approach enables an unbiased selection procedure overcoming a problem that is often encountered in CART: the bias to select variables with many possible splits or missing values [39].

2.7.2. Stopping Criteria

In addition to the stopping criteria of a minimum node size of 50 and a maximum depth of four described above, the algorithm also terminates if none of the covariates show a significant association with the target variable. In our analysis we set the p-value threshold to 0.05 and used a Bonferroni correction to adjust for multiple testing. Moreover, for CIT it is not considered necessary to prune the trees in a following step [20].

2.7.3. Random Forests to Calculate Variable Importance

One problem with using decision trees is that they can be vulnerable to random patterns in the data, and results may thus not always be reproducible in slightly different samples. It is therefore advisable to calculate the variable importance measure using random forests in order to evaluate whether the splitting variables found in the original CIT also have the highest variable importance values across an ensemble of trees [18,46]. Therefore, a random forest consisting of 500 trees was grown. Following a rule of thumb, we used six randomly selected covariates (i.e., the square-root of the overall number of covariates) for classification and 13 (i.e., one third of the overall number of covariates) in regression for each tree within the forest [49]. Variable importance was measured in terms of mean decrease in classification accuracy. Therefore, a covariate is randomly permuted over all trees breaking up the association with the response variable. If this covariate is associated with the response, prediction accuracy should decrease when using the permuted covariate to predict the response (see Strobl [50] for more details). For the interpretation of the resulting variable importance measures, Strobl [46] suggested selecting those covariates as informative that have a positive value, which is higher than the random variation around zero, i.e., positive values greater than the absolute value corresponding to the lowest negative value. We refer to Strobl [46] for a more detailed explanation.

2.8. Software

All analyses were performed in R using version 4.0.2. CART is implemented in the rpart package [38]. For the CIT analysis we used the ctree and cforest functions in the partykit package [40].

3. Results

3.1. Sample Characteristics

From 5256 KORA participants we received 3742 valid questionnaires, corresponding to a response rate of 71.2%. Of these, 2624 participants (70.1% of the whole INGER sample) were part of the KORA FIT study. The distributions of all 40 sex/gender covariates, which were included in our analyses are presented in Table 1 (see Supplementary Table S1 for distributions within the INGER KORA FIT sample). At birth, 53.9% were assigned a female sex and 45.0% a male sex, with 1.2% not answering this question. When asked about their current sex/gender identity, 53.4% of the participants classified themselves as female, 44.1% as male, 0.1% as trans, 0.1% as an identity that was not mentioned within the survey, and 0.4% did not want to be classified as any sex/gender category. As we also allowed multiple answers to this question, 0.1% of the participants answered with both female and that they did not want to classify as any sex/gender category, 0.2% answered with both male and that they did not want to classify as any sex/gender category, and 0.1% classified themselves as both male and an identity not mentioned within the survey. Furthermore, 1.6% did not give an answer to this question.
For exposure distributions within the INGER sample see Table 2 (see Supplementary Table S2 for distributions within the INGER KORA FIT sample).
A further description of the INGER study population is presented in Table 3 (see Supplementary Table S3 for distributions within the INGER KORA FIT sample). As only adults aged 45 or above took part in the survey, the mean age of the participants in the whole sample was 63.41 years and 47.7% were retired. Notably, the majority of participants had access to outdoor spaces, for example, 69.9% had access to a private garden, and a further 9.7% had access to a garden that they share with several parties. Furthermore, 71.7% had access to a balcony or terrace. Combining the answers to these questions showed that only 1.7% of the participants had no access to outdoor spaces at all, i.e., they had neither a garden nor balcony or terrace.

3.2. Access to Public Green Spaces (Subjectively Measured)

3.2.1. CART Results

Running a CART analysis for the exposure variable access to public green spaces with the 40 sex/gender covariates did not yield any splits, even though we used a quite low cp value of 0.001 (see Supplementary Materials S1, pp. 2–4).

3.2.2. CIT Results

Running a CIT analysis for the exposure variable access to public green spaces with the 40 sex/gender covariates resulted in a tree with two splits and three subgroups based on the covariates SGRelationsIncome and SGIdentity. Importantly, however, the cforest analysis with 500 trees showed that none of the covariates should be further investigated according to the variable importance score threshold suggested by Strobl [46], thus the identified tree has to be interpreted with caution (see Supplementary Materials S1, pp. 4–6).

3.3. Access to High Quality Public Green Space (Subjectively Measured)

3.3.1. CART Results

Running a CART analysis for the exposure variable access to high quality public green spaces with the 40 sex/gender covariates yielded a tree with three splits and four subgroups (see Supplementary Materials S1, pp. 7–11) after pruning with the minimum cross-validation error rule (pruning with the 1-SE rule would not have led to any splits). The first split was initiated by the participant’s experiences with age discrimination (DiscriminationAge). Those who had already been discriminated against because of their age formed the subgroup with least access to high quality public green spaces. The remaining participants were split again into those with a very good self-rated financial situation and those who rated their own financial situation as bad, moderate, or good (SGRelationsIncome). The first group showed a higher prevalence of access to high quality public green spaces and were split again according to the variable SGRolesHousewifeFulfilling. Variable importance measures indicate that DiscriminationAge has the highest variable importance followed by DiscriminationSocialPosition, SGRelationsIncome, and three other variables indicating discrimination experiences. SGRolesHousewifeFulfilling had a rather low value, this split should therefore be interpreted with caution.

3.3.2. CIT Results

Running a CIT analysis with the 40 sex/gender covariates for the exposure variable access to high quality public green space resulted in a tree with four splits and five subgroups (see Figure 1). Initially the population was split by the participant’s self-rated financial situation (SGRelationsIncome). Those with a bad or moderate rating were sent to one branch of the tree to be split again by degree of urbanization (SGRelationsUrbanisation). These two subgroups showed the lowest prevalence of access to high quality public green spaces. Participants with a good or very good self-rated financial situation were sent down a second tree branch where they were split by their experiences with age discrimination (DiscriminationAge) and once again by their self-rated financial situation (SGRelationsIncome). Thus, three different subgroups were formed: participants who stated they had already been discriminated against because of their age, those who had never experienced age discrimination and rated their self-rated financial situation as good and those who rated their financial situation as very good and had never experienced age discrimination. For the latter group, the highest prevalence of access to high quality green spaces was reported. As can be seen in Figure 1, this is the only subgroup where the proportions shifted, so that more participants had access to high quality green than to only lower quality green.
Conducting a test for variable importance with cforest also identified DiscriminationAge and SGRelationsIncome as the most important variables, followed by DiscriminationSocialPosition (Figure 2). Four other variables indicating discrimination experiences were also above the threshold suggested by Strobl [46]. However, the variable SGRelationsUrbanisation, that produced a split in our reported tree, had a variable importance score slightly below the threshold, thus this split should be interpreted with caution. In general, conducting the cforest analysis several times with different seeds showed that the only variables that were consistently above the threshold were DiscriminationAge, SGRelationsIncome and DiscriminationSocialPosition, while all other variables were at times above and at times below the threshold.

3.4. Greenness in the Residential Environment (Subjectively Measured)

3.4.1. CART Results

Running a CART analysis for the exposure variable greenness in the residential environment with the 40 sex/gender covariates did not yield any splits after pruning with the minimum cross-validation error rule (see Supplementary Materials S1, pp. 14–16).

3.4.2. CIT Results

Running a CIT analysis with the 40 sex/gender covariates for the exposure variable greenness in the residential environment resulted in a tree with seven splits and eight subgroups (see Supplementary Materials S1, pp. 16–18). The first splitting variable chosen was CareActivitiesGardening, dividing the population into participants answering “not applicable” versus all others. As the answer category “not applicable” was chosen by participants without a garden, this first split can be considered as a division of participants with versus without a garden. Those without a garden were split again by the participants’ self-rated financial situation (SGRelationsIncome). This led to two subgroups: participants with a bad or moderate self-rated financial situation and participants with a good or very good self-rated financial situation, the latter having a higher proportion of very green in the residential environment. Participants with a garden were sent down a second tree branch where they were split by degree of urbanization (SGRelationsUrbanisation). Participants who lived in a city were sent to one branch and those who lived in suburban or rural areas were sent to the other. Those from the city were split once again by their self-rated financial situation (SGRelationsIncome), with participants with a good or very good self-rated financial situation again showing a higher proportion of very green in the residential environment. Participants who lived in suburban or rural areas were further split by DiscriminationSocialPosition, SexAtBirth and once again SGRelationsUrbanisation. The cforest analysis with 500 trees showed that only the three covariates SGRelationsUrbanisation, CareActivitiesGardening and SGRelationsIncome should be further investigated according to the variable importance score threshold suggested by Strobl [46]. Therefore, the lower splits of the CIT tree described here must be interpreted with caution, as they included two covariates (DiscriminationSocialPosition and SexAtBirth), which showed a variable permutation importance value that was not higher than the random variation around zero.

3.5. Greenness within a 300 m Buffer around the Residential Address (Objectively Measured)

3.5.1. CART Results

Results from a CART analysis for the continuous exposure variable greenness within a 300 m buffer indicated a tree with four splits (see Supplementary Materials S1, pp. 19–22) after pruning with the minimum cross-validation error rule (pruning with the 1-SE rule would have led to a tree with two splits). The first split was performed by the degree of urbanization (SGRelationsUrbanisation). Participants living in a city were sent to one side of the tree and were split again according to SGRolesSingleParentEqual, forming the two subgroups with the lowest mean greenness. The rest of the population was split again into participants living in suburban and those living in rural areas (SGRelationsUrbanisation). While participants living in rural areas formed the subgroup with the highest mean greenness, participants in suburban areas were further split according to whether or not they have their own garden (CareActivitiesGardening), with participants having a garden showing a higher mean greenness. Variable importance measures indicated that SGRelationsUrbanisation and CareActivitiesGardening were by far the most important splitting variables. On the other hand, SGRolesSingleParentEqual had a comparably low value and this split should therefore be interpreted with caution.

3.5.2. CIT Results

Results from the CIT analysis for the continuous exposure variable greenness within a 300 m buffer indicated a tree with six splits leading to seven final subgroups (see Supplementary Materials S1, pp. 23–24). The primary split was based on the degree of urbanization (SGRelationsUrbanisation) sending participants living in a city to one branch and the rest of the population to the other one. The participants living in a city were split again according to the variable SGRolesSingleParentEqual resulting in the two subgroups with the lowest mean of greenness. Participants from suburban or rural areas were split once again based on SGRelationsUrbanisation. Participants from rural areas showed the highest mean greenness and were split again according to their school education (SGRelationsSchoolEducation). Participants living in suburban areas were further split by CareActivitiesGardening, with those without their own garden showing the lowest mean of greenness. Participants with a garden were split again based on their experiences with discrimination because of their sexual orientation (DiscriminationSexualOrientation). Conducting a variable importance analysis indicated that SGRelationsUrbanisation and CareActivitiesGardening had by far the highest importance. Four other variables were also above the threshold suggested by Strobl [46], however SGRelationsSchoolEducation, SGRolesSingleParentEqual and DiscriminationSexualOrientation were not amongst them, so that those three splits in the tree described above should be interpreted with caution. When conducting the cforest analysis with different seeds, the results were very stable for SGRelationsUrbanisation and CareActivitiesGardening, but also two other variables, SGRelationsFamilySituation and CareActivitiesChildren, were consistently above the threshold and always the third and fourth most important variables.

3.6. Greenness within a 1000 m Buffer around the Residential Address (Objectively Measured)

3.6.1. CART Results

Running a CART analysis with the 40 sex/gender covariates for the continuous exposure variable greenness within a 1000 m buffer resulted in a tree with three splits and four subgroups after pruning with the minimum cross-validation error rule (pruning with the 1-SE rule would have led to a tree with two splits).
As can be seen in Figure 3, the primary split was based on the degree of urbanization (SGRelationsUrbanisation) sending participants living in a city to one branch resulting in the subgroup with the lowest mean of greenness. Those living in suburban or rural areas were sent to the other branch and were split once again by degree of urbanization (SGRelationsUrbanisation). Participants living in rural areas had the highest mean of greenness whereas those living in suburban areas were split again by CareActivitiesGardening, with all participants without a garden, being sent to the subgroup with the second lowest mean of greenness. All participants with a garden were sent down the other tree branch resulting in the subgroup with the second highest mean of greenness. The variable importance measures showed that SGRelationsUrbanisation was by far the most important covariate, while CareActivitiesGardening was the second most important variable.

3.6.2. CIT Results

Running a CIT analysis with the 40 sex/gender covariates for the continuous exposure variable greenness within a 1000 m buffer resulted in a tree with seven splits and eight subgroups (see Supplementary Materials S1, pp. 28–30). The first two splits were both based on the degree of urbanization (SGRelationsUrbanisation), sending participants living in a city, those living in rural areas and those living in suburban areas down three different tree branches. Those living in a city were split again by SGRolesSameSexEqual, resulting in the two subgroups with the overall lowest mean of greenness. Participants living in rural areas were split twice by school education (SGRelationsSchoolEducation), resulting in the three subgroups with the overall highest mean of greenness. Participants living in suburban areas were split again by CareActivitiesGardening, dividing participants based on whether they had a garden or not. The subgroup of participants with a garden were split once more by discrimination based on their sexual orientation (DiscriminationSexualOrientation). The subgroup of participants without a garden had a lower mean of greenness compared to the other two subgroups in this tree branch. The variable importance measures showed that SGRelationsUrbanisation and CareActivitiesGardening were by far the most important covariates from in total seven variables that were above the variable importance threshold suggested by Strobl [46]. The covariate SGRelationsSchoolEducation that led to a split here was also above the threshold, but so were four other variables with similarly high variable importance values that did not produce a split. The splits based on SGRolesSameSexEqual and DiscriminationSexualOrientation must be interpreted with caution, as they showed a variable importance value that was not higher than the random variation around zero. When repeating the cforest analysis with different seeds, the results were only stable for SGRelationsUrbanisation and CareActivitiesGardening and the two variables with the next highest values: SGRelationsFamilySituation and CareActivitiesChildren.

3.7. Analyses with 53 Covariates for a Subsample of n = 2624 Participants

For the subsample INGER KORA FIT with 2624 participants, we re-ran all decision tree analyses with a total of 53 covariates as we had 13 additional covariates available for these participants (see Supplementary Table S1). Detailed results of these analyses can be found in Supplementary Materials S2. Overall, the results from this subsample confirmed the results from the analyses with the whole sample.
For the exposure measure access to high quality public green spaces, the first and most important splits were again based on the variables DiscriminationAge and SGRelationsIncome, with the variable importance measures suggesting that other variables indicating discrimination experiences were also of importance. Although two of the 13 additional variables led to splits in the trees for this exposure measure (i.e. HealthBehaviorAlcohol in the CART tree and SGRelationsMobility in the CIT tree), the variable importance measures showed that these variables were less important and the splits should be interpreted with caution.
For the exposure measure greenness in the residential environment, as well as the two NDVI measures, the results of the subsample confirmed the importance of SGRelationsUrbanisation and CareActivitiesGardening. Interestingly, the cforest analyses for both of the NDVI measures showed that besides the most dominant SGRelationsUrbanisation and CareActivitiesGardening, three other variables were consistently above the threshold of random variation: as in the whole sample these included SGRelationsFamilySituation and CareActivitiesChildren, but also the additional variable SGRelationsHouseholdMembers.

4. Discussion

Sex/gender is a multidimensional, non-binary, structural category, and can be comprehensively described within the multidimensional sex/gender concept, which we recently developed within the INGER project [9]. In order to adequately integrate sex/gender into quantitative research, statistical methods which can incorporate a high number of covariates, as well as their possible interactions, are required. We showed that decision trees fulfil these requirements and can be used to explore the relevance of multiple sex/gender dimensions for an environmental exposure. Using the exposure to green spaces in the residential environment as an exemplary field, we found that none of our covariates operationalizing the individual sex/gender self-concept (i.e., the dimensions sex assigned at birth, current sex/gender identity, internalized sex/gender roles and externalized sex/gender expressions) defined distinct subgroups with respect to the exposure to green spaces. However, we identified meaningful subgroups based on covariates contributing to explain structural sex/gender relations (i.e., discrimination experiences and intersectionality-related social categories). Thus, structural aspects related to sex/gender seem to play the most important role for differences in exposure to green spaces.

4.1. Methodological Considerations

4.1.1. CART vs. CIT

We applied two different decision tree algorithms, CART and CIT. Both methods have certain advantages. It has been shown that CART yields a slightly lower prediction error than CIT and therefore has a higher predictive accuracy [14]. However, as CART considers all splitting points of all covariates simultaneously it has been argued that CART may have a bias to select variables with many possible splitting points or missings [39]. CIT was explicitly developed to overcome this bias by using a two-step approach. Firstly, the best splitting covariate is selected by testing for independence of the exposure measure. Secondly, the best splitting point is determined [39]. Venkatasubramaniam [15] pointed out that CIT is simpler to use than CART as it requires less parameter tuning and no pruning. They further argued that another advantage of CIT is that it relies on a concept of statistical significance based on valid p-values, providing the ability to make formal statistical statements of the results [15]. However, as Nembrini [36] pointed out, this last argument can also be seen as a disadvantage for research that is in general critical of the null hypothesis testing framework. As Gass [20] elaborates, the decision whether to choose CART or CIT may also depend on the research question and purpose of the study, stating that CART is the best option when the goal is classification or prediction, while CIT is better when the goal is to find the covariates showing the strongest association with the dependent variable. However, both are useful to identify complex interactions [20], which was our focus considering our intersectional perspective. Our results showed that if there is a covariate that clearly leads to the best split, as is the case for SGRelationsUrbanisation and CareActivitiesGardening in the analyses for the two NDVI exposure measures, or SGRelationsIncome and DiscriminationAge for the exposure access to high quality public green, then this split is mostly identified by both CART and CIT. However, in one case, i.e., the subjectively measured greenness in the residential environment measure, CART led to no splits after pruning, while CIT identified SGRelationsUrbanisation, CareActivitiesGardening and SGRelationsIncome for splitting. In this case CART was too conservative, as CIT identified meaningful splits. In general, our results showed that when using the 1-SE rule for pruning CART led to no surviving splits, except for the first two splits based on SGRelationsUrbanisation for the two continuous NDVI exposure variables. This is rather conservative, and one might miss meaningful splits such as the ones based on the variable CareActivitiesGardening. Venkatasubramaniam [15] came to the same conclusion in their simulation study, recommending using the less conservative minimum cross-validation error rule for pruning. Overall, CIT led to trees with more splits and subgroups, however the cforest analyses with the variable importance measures then often showed that the additional splits must be interpreted with caution. The main conclusions from our results are therefore mostly the same for both CART and CIT.

4.1.2. Considering Variable Importance Measures

Our results additionally showed that it is fundamental to consider variable importance measures when interpreting the results of single decision trees. As has been elaborated, single trees can be unstable and may be influenced by small changes in the sample [14,46]. Sometimes the choice between two similar variables depends on minor differences in samples and only considering the covariates included in the final tree can undermine the importance of additional covariates that have a meaningful influence on the dependent variable and would appear in trees in a slightly different sample. For example, in our analyses for the exposure variable access to high quality public green space, both CART and CIT included the covariate DiscriminationAge, which might imply that this variable is of particular importance. However, a closer look at the variable importance measures revealed that other discrimination variables, especially DiscriminationSocialPosition, were of similar importance. On the other hand, we often identified a split in our single trees, only for the variable importance measures to show that the splitting variable is of low importance, suggesting that this split may not be reproducible in a slightly different sample. Researchers should therefore avoid reporting only a single tree as their main result without giving any further information about variable importance.

4.1.3. Exploratory Research

In general, decision tree analyses are exploratory and not suited to test hypotheses [16]. In our analyses we used covariates based on a newly established sex/gender questionnaire. We therefore had to use exploratory methods, as we were investigating new associations and did not have any a priori hypotheses about which sex/gender dimension may be of relevance for the availability of or access to green spaces. Decision trees are ideal to potentially find subgroups with particularly high or low exposure levels and to identify interactions that may not have been considered before. Nevertheless, we should keep in mind that this is hypothesis generating research and any conclusions must be tested in an independent sample in a next step.

4.1.4. Benefits of Decision Trees

We identified several benefits of using decision trees for future analyses including multiple sex/gender covariates. Firstly, decision trees can deal with many covariates simultaneously, which is decisive for our multidimensional sex/gender approach [9]. Secondly, decision trees can identify subgroups defined by different combinations of covariates, which is essential for our intersectional approach [9]. While it is possible to include interaction terms in regression models, they can become very difficult to interpret when more than two variables are assessed at the same time [19]. For instance, for a higher number of covariates, a priori knowledge is required since it becomes necessary to pre-specify what interactions to test for [14]. This may lead to missing important interactions not thought of beforehand [13]. In addition, while decision trees have the ability to segment populations into meaningful subgroups, standard regression models focus on the effect of a covariate on the average member of a population [19]. Moreover, decision tree methods are non-parametric and no distributional assumptions have to be checked. Another important advantage of decision tree methods compared to standard regression models is that they can handle missing values in the covariates without excluding participants. This becomes more important the higher the number of covariates is, as the number of participants with at least one missing value increases. A complete case analysis as in classical regression usually excludes too many participants. For instance, in our case sample size would be reduced to N = 2534, leaving a third of the observations unused. Finally, decision trees are easy to interpret and intuitive. The visualization allows the reader to easily capture the subgroup structure and directly compare the different outcome distributions.

4.2. Relevance of Sex/Gender Dimensions for the Exposure to Green Spaces

For the exposure measure access to public green spaces, no subgroups characterized by sex/gender were found, which could be expected due to the homogeneous distribution of this exposure measure with 90.4% of the study population having access to public green spaces. Previous research in the United States suggests that white and wealthier communities often had more access to urban public green spaces such as parks whereas racial or ethnic minorities and people with low-income had less [32]. Studies in cities of the Global South also found similar results [30]. In contrast to studies in large cities, KORA participants live in the medium sized city of Augsburg (approx. 300,000 inhabitants) or its surrounding rural areas. In general, our sample had a rather high exposure to public green spaces and nearly 80% of the participants had access to a garden.
Regarding access to high quality public green spaces, both CART and CIT identified the self-rated financial situation (SGRelationsIncome) and discrimination experience based on age (DiscriminationAge) as best splitting variables. A closer look at the variable importance measures revealed that other discrimination variables, especially DiscriminationSocialPosition, are of similar importance and also would have split the group into participants with discrimination experience versus participants without. Thus, it seems that discrimination experiences based on different reasons, as assessed by our questions, were of similar importance for the access to high quality public green spaces. Participants with the highest prevalence of access to public green spaces of high quality rated their financial situation as very good and had no discrimination experiences, as assessed by our questions. These results were in line with previous research suggesting that the quality of parks is lower in areas of low-income earners and ethnic minorities than in wealthier neighborhoods [51,52]. It is interesting that we were able to detect results with the same tendency in our sample, even though the social divide between our participants was not as pronounced as in other studies, e.g., only 1.8% of our participants rated their financial situation as bad. Nevertheless, the slight difference between rating one’s financial situation as very good compared to good already influenced access to high or lower quality parks.
Our final three exposure measurements reflected the general greenness in the residential environment, either subjectively measured or using NDVI data with two different buffers. For all three analyses, two covariates were identified as the most important: the degree of urbanization (SGRelationsUrbanisation) and the covariate CareActivitiesGardening. We chose our covariates based on our multidimensional sex/gender concept [9]. CareActivitiesGardening was initially intended to capture the amount of work participants invest in gardening, in a sense of caring about work that must be carried out around the house. However, as the question = also included the answer option “not applicable” for participants without a garden, we unintentionally gave the decision tree algorithm the option to split participants into a subgroup having a garden and a second group without a garden. Thus, the variable CareActivitiesGardening turned into a proxy for the ownership of a garden. SGRelationsUrbanisation was included as a contextual intersectionality-related social category with the intention of identifying possible interactions between the dimensions representing the individual sex/gender self-concept and the degree of urbanization. Not surprisingly, splits based on these two covariates revealed the following results: participants in cities had the lowest amount of greenness, with participants in the rural areas having the most. Participants with a garden had higher greenness scores than participants without. Although this may not lead to new hypotheses regarding the relevance of sex/gender dimensions for the exposure to greenness, it verified the ability of decision trees to find meaningful splits in the data. Moreover, one has to keep in mind that CareActivitiesGardening did not lead to any splits in the trees for the two exposure variables capturing the access to (high quality) public green spaces. This result again showed the meaningfulness of the trees, since having a garden did not directly influence the access to public green spaces. For the subjectively measured greenness variable, but not for the NDVI measures, other meaningful splits were based on the covariate SGRelationsIncome, showing higher subjective greenness ratings for participants who rated their financial situation as good or very good. Another difference between the subjective and objective measures was, that for the subjective greenness the first split was based on CareActivitiesGardening, while for the two NDVI measurements the first two splits were elicited by SGRelationsUrbanisation. Thus, having a garden or not was most decisive for the subjective feeling of greenness in the residential environment, while the degree of urbanization had the biggest influence on the objectively measured greenness in a 300 or 1000 m buffer.
For both of the NDVI measures the random forest analyses identified further informative covariates, i.e., CareActivitiesChildren and SGRelationsFamilySituation, as well as the additional variable SGRelationsHouseholdMembers in the KORA FIT sample. However, none of these variables led to splits in the single tree analyses, thus we could not directly interpret their influence on the objective exposure to green spaces. Importantly, in our KORA sample, the covariate CareActivitiesChildren mostly referred to care activity for grand-children as the sample consisted of mainly older adults (mean = 63.4 years, ranging from 43 to 92 years). Therefore, our sample hardly included participants with young children, i.e., participants in the reproductive phase of their life. The age structure of the sample might have had an impact on the relevance of some of the sex/gender covariates, as the reproductive phase, i.e., the period of gender-segregated, unpaid family care work, represents an important part of the gender inequality relations [53]. For future studies it would be interesting to examine whether covariates such as CareActivitiesChildren might have had a greater influence on the final results in samples including more participants in the reproductive phase.
Taken together, in our study primarily structural aspects related to sex/gender, such as material situation and urban/rural context, but no covariates representing the individual sex/gender self-concept were relevant for differences in exposure to public green space or greenness in the residential environment. This is in line with current evidence on social inequalities in environmental exposures such as green spaces [30,31,32].

4.3. Future Research

Previous research on possible sex/gender differences focused on the usage of public green spaces and parks, discussing the relevance of differences between women and men in care activities for children or the elderly [54] or in concerns about personal safety [33,35]. Future research exploring the relevance of multiple sex/gender dimensions for the usage of public green spaces may therefore add to these results obtained with a binary sex/gender category.
Within the INGER project the next step will be to explore whether multiple sex/gender covariates modify the effect of green spaces on health, using another type of decision tree algorithm, i.e., model-based recursive partitioning [55]. Exploring subgroups with differential exposure-outcome relationships will allow us to move from the descriptive intersectional approach applied in the current study to a more analytic intersectional approach as defined by Bauer and Scheim [56].

4.4. Strengths and Limitations

As it is always the case for observational studies, our study has some limitations. The study population is rather homogeneous in terms of age, ethnicity, social disparities and availability of private gardens. Quality of public green spaces was rated subjectively by respondents and we defined “high quality” rather strictly based on responses to questions on maintenance and quality assessment. Furthermore, based on feedback from participants, we can assume that some exposure misclassification might have occurred when participants in rural areas negated having access to public green spaces, as they did not interpret privately owned forests or meadows as green spaces publicly available to them. Moreover, we only dealt with static green space exposure measures based on the participants’ place of residence, not considering human mobility, i.e., spatiotemporal changes of participants’ locations during daily routines [28,57].
The strengths of our study are the well-characterized KORA study population and the high response rate of our KORA INGER survey, the comprehensive assessment of sex/gender dimensions with at least 40 covariates based on a theoretically substantiated concept, and the subjective and objective measurement of exposure to green spaces or greenness. We also used a comparative statistical analysis applying two different decision tree algorithms, CART and CIT, with consideration of variable importance measures to avoid overinterpretation of spurious findings.

5. Conclusions

Most importantly, our study showed that decision tree analyses are suitable methods to analyze complex data in order to explore the relevance of multiple sex/gender dimensions for environmental exposures. With respect to our analyses exploring the relevance of multiple sex/gender dimensions for the exposure to green spaces, we showed that the participants’ financial situation and discrimination experience was relevant for their access to high quality public green spaces, while the urban/rural context was most important for the general greenness in the residential environment. The covariates operationalizing the individual sex/gender self-concept did not lead to homogeneous subgroups with respect to the exposure to green spaces. It is important to consider that this study was performed with a rather homogeneous study population in a non-metropolitan context. Further studies in larger urban areas with less private gardens and more different forms of public green spaces, and with a study population more heterogeneous with respect to age and social disparities, would add to the evidence on possible sex/gender exposure differentials. Moreover, besides exposure metrics, usage of green spaces should also be taken into account.

Supplementary Materials

The following supporting information can be downloaded at: www.mdpi.com/article/10.3390/ijerph19127476/s1, Supplementary Materials S1: R-Code and detailed results with 40 Covariates, Supplementary Materials S2: R-Code and detailed results with 53 Covariates; Supplementary Materials S3: Contains the Supplementary Tables S1–S3 and cites the Refs. [58,59,60].

Author Contributions

L.D.: Conceptualization, Methodology, Formal Analysis, Data Curation, Writing—Original Draft, Visualization, Project Administration. C.H.: Methodology, Writing—Original Draft, Visualization, Project Administration. K.T.: Methodology, Formal Analysis, Writing—Original Draft, Visualization. S.H.: Methodology, Writing—Original Draft, Visualization, Project Administration. L.S.: Investigation, Resources, Writing—Review & Editing. P.S.: Resources, Data Curation, Writing—Review & Editing. A.S.: Conceptualization, Investigation, Resources, Writing—Review & Editing, Funding Acquisition. G.B.: Conceptualization, Methodology, Resources, Writing—Review & Editing, Supervision, Project Administration, Funding Acquisition. All authors have read and agreed to the published version of the manuscript.

Funding

The collaborative research project INGER—“Integrating gender into environmental health research” (https://www.uni-bremen.de/en/inger/) (accessed on 25 May 2022) is funded by the German Federal Ministry of Education and Research (funding number: 01GL1713). The KORA study was initiated and financed by the Helmholtz Zentrum München—German Research Center for Environmental Health, which is funded by the German Federal Ministry of Education and Research (BMBF) and by the State of Bavaria.

Institutional Review Board Statement

The KORA studies were approved by the Ethics Committees of the Bavarian Chamber of Physicians (KORA-Fit EC No 17040).

Informed Consent Statement

Written informed consent was obtained from all participants involved in the study.

Data Availability Statement

The data that support the findings of this study are available from the KORA study team of the Helmholtz Zentrum München but restrictions apply to the availability of these data, which were used under license for the current study, and so are not publicly available.

Acknowledgments

We thank Annette Peters for critical reading of the manuscript and valuable comments. INGER Study Group: University of Bremen, Institute of Public Health and Nursing Research, Department of Social Epidemiology, Bremen, Germany (Gabriele Bolte, Lisa Dandolo, Christina Hartig, Sophie Horstmann, Klaus Telkmann); Helmholtz Zentrum München, German Research Center for Environmental Health (GmbH), Institute of Epidemiology, Neuherberg, Germany (Ute Kraus, Alexandra Schneider); German Environment Agency, Section II 1.2 Toxicology, Health-related Environmental Monitoring, Berlin, Germany (Malgorzata Debiak, Katrin Groth, Sophie Fichter, Marike Kolossa-Gehring); Humboldt-University of Berlin, Institute of History, Gender and Science research unit, Berlin, Germany (Katharina Jacke, Kerstin Palm).

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Bolte, G.; David, M.; Debiak, M.; Fiedel, L.; Hornberg, C.; Kolossa-Gehring, M.; Kraus, U.; Latzsch, R.; Paeck, T.; Palm, K.; et al. Integration of sex/gender into environmental health research. Results of the interdisciplinary research network Sex/Gender-Environment-Health (GeUmGe-NET). Bundesgesundheitsbla 2018, 61, 737–746. [Google Scholar] [CrossRef] [PubMed]
  2. Bolte, G.; Nanninga, S.; Dandolo, L. Sex/Gender Differences in the Association between Residential Green Space and Self-Rated Health-A Sex/Gender-Focused Systematic Review. Int. J. Environ. Res. Public Health 2019, 16, 4818. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  3. Cantarero, L.; Aguirre, I.Y. Gender Inequities in Environment and Health. Environment and Health Risks: A Review of the Influence and Effects of Social Inequalities; WHO Regional Office for Europe: Copenhagen, Denmark, 2010. [Google Scholar]
  4. Clougherty, J.E. A Growing Role for Gender Analysis in Air Pollution Epidemiology. Environ. Health Perspect. 2010, 118, 167–176. [Google Scholar] [CrossRef] [Green Version]
  5. Hammarström, A.; Johansson, K.; Annandale, E.; Ahlgren, C.; Alex, L.; Christianson, M.; Elwer, S.; Eriksson, C.; Fjellman-Wiklund, A.; Gilenstam, K.; et al. Central gender theoretical concepts in health research: The state of the art. J. Epidemiol. Community Health 2014, 68, 185–190. [Google Scholar] [CrossRef] [PubMed]
  6. Johnson, J.L.; Greaves, L.; Repta, R. Better science with sex and gender: Facilitating the use of a sex and gender-based analysis in health research. Int. J. Equity Health 2009, 8, 14. [Google Scholar] [CrossRef] [Green Version]
  7. Krieger, N. Genders, sexes, and health: What are the connections—And why does it matter? Int. J. Epidemiol. 2003, 32, 652–657. [Google Scholar] [CrossRef]
  8. Phillips, S.P. Measuring the health effects of gender. J. Epidemiol. Community Health 2008, 62, 368–371. [Google Scholar] [CrossRef]
  9. Bolte, G.; Jacke, K.; Groth, K.; Kraus, U.; Dandolo, L.; Fiedel, L.; Debiak, M.; Kolossa-Gehring, M.; Schneider, A.; Palm, K. Integrating Sex/Gender into Environmental Health Research: Development of a Conceptual Framework. Environ. Res. Public Health 2021, 18, 12118. [Google Scholar] [CrossRef]
  10. Springer, K.W.; Stellman, J.M.; Jordan-Young, R.M. Beyond a catalogue of differences: A theoretical frame and good practice guidelines for researching sex/gender in human health. Soc. Sci. Med. 2012, 74, 1817–1824. [Google Scholar] [CrossRef]
  11. Bauer, G.R. Incorporating intersectionality theory into population health research methodology: Challenges and the potential to advance health equity. Soc. Sci. Med. 2014, 110, 10–17. [Google Scholar] [CrossRef] [Green Version]
  12. Merz, S.; Jaehn, P.; Mena, E.; Poge, K.; Strasser, S.; Sass, A.C.; Rommel, A.; Bolte, G.; Holmberg, C. Intersectionality and eco-social theory: A review of potentials for public health knowledge and social justice. Crit. Public Health 2021, 1–10. [Google Scholar] [CrossRef]
  13. Lei, Y.; Nollen, N.; Ahluwahlia, J.S.; Yu, Q.; Mayo, M.S. An application in identifying high-risk populations in alternative tobacco product use utilizing logistic regression and CART: A heuristic comparison. BMC Public Health 2015, 15, 341. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  14. Wolfson, J.; Venkatasubramaniam, A. Branching Out: Use of Decision Trees in Epidemiology. Curr. Epidemiol. Rep. 2018, 5, 221–229. [Google Scholar] [CrossRef]
  15. Venkatasubramaniam, A.; Wolfson, J.; Mitchell, N.; Barnes, T.; JaKa, M.; French, S. Decision trees in epidemiological research. Emerg. Themes Epidemiol. 2017, 14, 11. [Google Scholar] [CrossRef]
  16. Cairney, J.; Veldhuizen, S.; Vigod, S.; Streiner, D.L.; Wade, T.J.; Kurdyak, P. Exploring the social determinants of mental health service use using intersectionality theory and CART analysis. J. Epidemiol. Community Health 2014, 68, 145–150. [Google Scholar] [CrossRef]
  17. Mena, E.; Bolte, G.; AdvanceGender Study Group. CART-analysis embedded in social theory: A case study comparing quantitative data analysis strategies for intersectionality-based public health monitoring within and beyond the binaries. SSM Popul. Health 2021, 13, 100722. [Google Scholar] [CrossRef]
  18. Winkler, M.R.; Telke, S.; Ahonen, E.Q.; Crane, M.M.; Mason, S.M.; Neumark-Sztainer, D. Constrained choices: Combined influences of work, social circumstances, and social location on time-dependent health behaviors. SSM Popul. Health 2020, 11, 100562. [Google Scholar] [CrossRef]
  19. Lemon, S.C.; Roy, J.; Clark, M.A.; Friedmann, P.D.; Rakowski, W. Classification and regression tree analysis in public health: Methodological review and comparison with logistic regression. Ann. Behav. Med. 2003, 26, 172–181. [Google Scholar] [CrossRef]
  20. Gass, K.; Addiss, D.G.; Freeman, M.C. Exploring the relationship between access to water, sanitation and hygiene and soil-transmitted helminth infection: A demonstration of two recursive partitioning tools. PLoS Negl. Trop. Dis. 2014, 8, e2945. [Google Scholar] [CrossRef] [Green Version]
  21. Henrard, S.; Speybroeck, N.; Hermans, C. Classification and regression tree analysis vs. multivariable linear and logistic regression methods as statistical tools for studying haemophilia. Haemophilia 2015, 21, 715–722. [Google Scholar] [CrossRef]
  22. Nayak, S.; Hubbard, A.; Sidney, S.; Syme, S.L. A recursive partitioning approach to investigating correlates of self-rated health: The CARDIA Study. SSM Popul. Health 2018, 4, 178–188. [Google Scholar] [CrossRef] [PubMed]
  23. Gianfredi, V.; Buffoli, M.; Rebecchi, A.; Croci, R.; Oradini-Alacreu, A.; Stirparo, G.; Marino, A.; Odone, A.; Capolongo, S.; Signorelli, C. Association between Urban Greenspace and Health: A Systematic Review of Literature. Int. J. Environ. Res. Public Health 2021, 18, 5137. [Google Scholar] [CrossRef] [PubMed]
  24. Hunter, R.F.; Cleland, C.; Cleary, A.; Droomers, M.; Wheeler, B.W.; Sinnett, D.; Nieuwenhuijsen, M.J.; Braubach, M. Environmental, health, wellbeing, social and equity effects of urban green space interventions: A meta-narrative evidence synthesis. Environ. Int. 2019, 130, 104923. [Google Scholar] [CrossRef] [PubMed]
  25. Nieuwenhuijsen, M.J. Green Infrastructure and Health. Annu. Rev. Public Health 2021, 42, 317–328. [Google Scholar] [CrossRef]
  26. Rigolon, A.; Browning, M.H.E.M.; McAnirlin, O.; Yoon, H. Green Space and Health Equity: A Systematic Review on the Potential of Green Space to Reduce Health Disparities. Int. J. Environ. Res. Public Health 2021, 18, 2563. [Google Scholar] [CrossRef]
  27. Hankey, S.; Marshall, J.D. Urban Form, Air Pollution, and Health. Curr. Environ. Health Rep. 2017, 4, 491–503. [Google Scholar] [CrossRef]
  28. Kondo, M.C.; Fluehr, J.M.; McKeon, T.; Branas, C.C. Urban Green Space and Its Impact on Human Health. Int. J. Environ. Res. Public Health 2018, 15, 445. [Google Scholar] [CrossRef] [Green Version]
  29. World Health Organization (WHO). Urban Green Spaces and Health; WHO Regional Office for Europe: Copenhagen, Denmark, 2016. [Google Scholar]
  30. Rigolon, A.; Browning, M.H.E.M.; Lee, K.; Shin, S. Access to Urban Green Space in Cities of the Global South: A Systematic Literature Review. Urban Sci. 2018, 2, 67. [Google Scholar] [CrossRef] [Green Version]
  31. Schüle, S.A.; Hilz, L.K.; Dreger, S.; Bolte, G. Social Inequalities in Environmental Resources of Green and Blue Spaces: A Review of Evidence in the WHO European Region. Int. J. Environ. Res. Public Health 2019, 16, 1216. [Google Scholar] [CrossRef] [Green Version]
  32. Wolch, J.R.; Byrne, J.; Newell, J.P. Urban green space, public health, and environmental justice: The challenge of making cities ‘just green enough’. Landsc. Urban Plan. 2014, 125, 234–244. [Google Scholar] [CrossRef] [Green Version]
  33. Derose, K.P.; Han, B.; Williamson, S.; Cohen, D.A. Gender Disparities in Park Use and Physical Activity among Residents of High-Poverty Neighborhoods in Los Angeles. Women’s Health Issues 2018, 28, 6–13. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  34. Lee, A.C.; Maheswaran, R. The health benefits of urban green spaces: A review of the evidence. J. Public Health 2011, 33, 212–222. [Google Scholar] [CrossRef] [PubMed]
  35. Richardson, E.A.; Mitchell, R. Gender differences in relationships between urban green space and health in the United Kingdom. Soc. Sci. Med. 2010, 71, 568–575. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  36. Nembrini, S. Prediction or interpretability? Emerg. Themes Epidemiol. 2019, 16, 4. [Google Scholar] [CrossRef] [PubMed]
  37. Breiman, L.; Friedman, J.; Stone, C.J.; Olshen, R.A. Classification and Regression Trees; Taylor & Francis: Abingdon, UK, 1984. [Google Scholar]
  38. Therneau, T.; Atkinson, E. An Introduction to Recursive Partitioning Using the RPART Routines; Mayo Foundation: Rochester, MN, USA, 2019. [Google Scholar]
  39. Hothorn, T.; Hornik, K.; Zeileis, A. Unbiased Recursive Partitioning: A Conditional Inference Framework. J. Comput. Graph. Stat. 2006, 15, 651–674. [Google Scholar] [CrossRef] [Green Version]
  40. Hothorn, T.; Zeileis, A. Partykit: A modular toolkit for recursive partytioning in R. J. Mach. Learn. Res. 2015, 16, 3905–3909. [Google Scholar]
  41. Holle, R.; Happich, M.; Lowel, H.; Wichmann, H.E.; Group, M.K.S. KORA—A research platform for population based health research. Gesundheitswesen 2005, 67 (Suppl. 1), 19–25. [Google Scholar] [CrossRef] [Green Version]
  42. Tucker, C.J. Red and Photographic Infrared Linear Combinations for Monitoring Vegetation. Remote Sens. Environ. 1979, 8, 127–150. [Google Scholar] [CrossRef] [Green Version]
  43. Markevych, I.; Thiering, E.; Fuertes, E.; Sugiri, D.; Berdel, D.; Koletzko, S.; von Berg, A.; Bauer, C.-P.; Heinrich, J. A cross-sectional analysis of the effects of residential greenness on blood pressure in 10-year old children: Results from the GINIplus and LISAplus studies. BMC Public Health 2014, 14, 477. [Google Scholar] [CrossRef] [Green Version]
  44. Weier, J.; Herring, D. Measuring Vegetation (NDVI & EVI). 2000. Available online: https://earthobservatory.nasa.gov/features/MeasuringVegetation (accessed on 8 October 2020).
  45. Buchhorn, M.; Lesiv, M.; Tsendbazar, N.E.; Herold, M.; Bertels, L.; Smets, B. Copernicus Global Land Cover Layers-Collection 2. Remote Sens. 2020, 12, 1044. [Google Scholar] [CrossRef] [Green Version]
  46. Strobl, C.; Malley, J.; Tutz, G. An introduction to recursive partitioning: Rationale, application, and characteristics of classification and regression trees, bagging, and random forests. Psychol. Methods 2009, 14, 323–348. [Google Scholar] [CrossRef] [Green Version]
  47. Harper, P.R. A review and comparison of classification algorithms for medical decision making. Health Policy 2005, 71, 315–331. [Google Scholar] [CrossRef] [PubMed]
  48. Speybroeck, N. Classification and regression trees. Int. J. Public Health 2012, 57, 243–246. [Google Scholar] [CrossRef]
  49. Liaw, A.; Wiener, M. Classification and regression by randomForest. R News 2002, 2, 18–22. [Google Scholar]
  50. Strobl, C.; Boulesteix, A.L.; Zeileis, A.; Hothorn, T. Bias in random forest variable importance measures: Illustrations, sources and a solution. BMC Bioinform. 2007, 8, 25. [Google Scholar] [CrossRef] [Green Version]
  51. Heynen, N.; Perkins, H.A.; Roy, P. The political ecology of uneven urban green space—The impact of political economy on race and ethnicity in producing environmental inequality in Milwaukee. Urban Aff. Rev. 2006, 42, 3–25. [Google Scholar] [CrossRef]
  52. Rigolon, A. A complex landscape of inequity in access to urban parks: A literature review. Landsc. Urban Plan. 2016, 153, 160–169. [Google Scholar] [CrossRef]
  53. Wrohlich, K. Gender Care Gap: Sorgearbeit gerecht verteilen. Wirtschaftsdienst 2021, 101, 748. [Google Scholar] [CrossRef]
  54. Tamosiunas, A.; Grazuleviciene, R.; Luksiene, D.; Dedele, A.; Reklaitiene, R.; Baceviciene, M.; Vencloviene, J.; Bernotiene, G.; Radisauskas, R.; Malinauskiene, V.; et al. Accessibility and use of urban green spaces, and cardiovascular health: Findings from a Kaunas cohort study. Environ. Health 2014, 13, 20. [Google Scholar] [CrossRef] [Green Version]
  55. Zeileis, A.; Hothorn, T.; Hornik, K. Model-based recursive partitioning. J. Comput. Graph. Stat. 2008, 17, 492–514. [Google Scholar] [CrossRef] [Green Version]
  56. Bauer, G.R.; Scheim, A.I. Methods for analytic intercategorical intersectionality in quantitative research: Discrimination as a mediator of health inequalities. Soc. Sci. Med. 2019, 226, 236–245. [Google Scholar] [CrossRef] [PubMed]
  57. Song, Y.; Huang, B.; Cai, J.; Chen, B. Dynamic assessments of population exposure to urban greenspace using multi-source big data. Sci. Total Environ. 2018, 634, 1315–1325. [Google Scholar] [CrossRef] [PubMed]
  58. Klein, E.M.; Brahler, E.; Dreier, M.; Reinecke, L.; Muller, K.W.; Schmutzer, G.; Wolfling, K.; Beutel, M.E. The German version of the Perceived Stress Scale—Psychometric characteristics in a representative German community sample. BMC Psychiatry 2016, 16, 159. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  59. Beierlein, C.; Kovaleva, A.; Kemper, C.J.; Rammstedt, B. ASKU—Allgemeine Selbstwirksamkeit Kurzskala [Fragebogen]; Elektronisches Testarchiv (PSYNDEX Tests-Nr. 9006490); Leibniz-Zentrum für Psychologische Information und Dokumentation (ZPID): Trier, Germany, 2012. [Google Scholar]
  60. Glaesmer, H.; Hoyer, J.; Klotsche, J.; Herzberg, P.Y. The German version of the Life-Orientation-Test (LOT-R) for dispositional optimism and pessimism. Z. Gesundh. 2008, 16, 26–31. [Google Scholar] [CrossRef] [Green Version]
Ijerph 19 07476 g001 550
Figure 1. CIT tree for the exposure measure access to high quality public green space (subjectively measured). Bars in the bottom row show the proportion of participants in each exposure category.
Figure 1. CIT tree for the exposure measure access to high quality public green space (subjectively measured). Bars in the bottom row show the proportion of participants in each exposure category.
Ijerph 19 07476 g001
Ijerph 19 07476 g002 550
Figure 2. Variable importance measures calculated using random forest for the exposure measure access to high quality public green spaces. Values on the x-axis indicate mean decrease in accuracy for each covariate after random permutations. Bars colored in the darker shade correspond to variable importance values higher than the random variation around zero, a threshold for identifying informative variables suggested by Strobl [46].
Figure 2. Variable importance measures calculated using random forest for the exposure measure access to high quality public green spaces. Values on the x-axis indicate mean decrease in accuracy for each covariate after random permutations. Bars colored in the darker shade correspond to variable importance values higher than the random variation around zero, a threshold for identifying informative variables suggested by Strobl [46].
Ijerph 19 07476 g002
Ijerph 19 07476 g003 550
Figure 3. CART tree for the exposure measure greenness within a 1000 m buffer around the residential address (objectively measured). Boxplots in the bottom row show the distribution of the NDVI values in each subgroup.
Figure 3. CART tree for the exposure measure greenness within a 1000 m buffer around the residential address (objectively measured). Boxplots in the bottom row show the distribution of the NDVI values in each subgroup.
Ijerph 19 07476 g003
Table
Table 1. The 40 Sex/Gender Covariates. Distributions within the INGER sample.
Table 1. The 40 Sex/Gender Covariates. Distributions within the INGER sample.
Covariate Name and Question *
in INGER KORA Survey		Answer Categories and Distribution in the Whole Sample;
N = 3742 (100%) #
Individual sex/gender self-concept
Sex assigned at birth
SexAtBirth
What sex were you assigned at birth? 		2014 (53.8)
1684 (45.0)
44 (1.2)		 = female
= male
= missing
Current sex/gender identity
SGIdentity
What is your current sex/gender identity?
(Multiple answers possible) 		1998 (53.4)
1650 (44.1)
0 (0.0)
2 (0.1)
4 (0.1)
14 (0.4)
3 (0.1)
4 (0.1)
7 (0.2)
60 (1.6)		 = female
= male
= intersexual
= trans, trans man, trans woman
= an identity not mentioned here
= I do not want to classify as any SG category
= female AND I do not want to classify as any SG category
= male AND an identity not mentioned here
= male AND I do not want to classify as any SG category
= missing
Internalized sex/gender roles
SGRolesFemMascuFeeling
I mostly perceive myself as …		403 (10.8)
866 (23.1)
303 (8.1)
426 (11.4)
173 (4.6)
958 (25.6)
436 (11.7)
177 (4.7)		 = very masculine
= mainly masculine
= a little masculine
= just as feminine as masculine
= a little feminine
= mainly feminine
= very feminine
= missing
SGRolesFemMascuWish
Ideally, I would like to be...		482 (12.9)
844 (22.6)
196 (5.2)
384 (10.3)
151 (4.0)
878 (23.5)
550 (14.7)
257 (6.9)		 = very masculine
= mainly masculine
= a little masculine
= just as feminine as masculine
= a little feminine
= mainly feminine
= very feminine
= missing
SGRolesFemMascuChange
Has your assessment of what is feminine or masculine changed in recent years?		382 (10.2)
3206 (85.7)
154 (4.1)		 = yes
= no
= missing
SGRolesBothIncomeContribute
Both the men and women should contribute to the household income.		1766 (47.2)
990 (26.5)
801 (21.4)
95 (2.5)
33 (0.9)
57 (1.5)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesMenMoneyWomenHouse
The man’s job is to earn money; a woman’s job is to look after the home and family.		106 (2.8)
293 (7.8)
898 (24.0)
1010 (27.0)
1380 (36.9)
55 (1.5)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesGoodRelationshipWorkingMom
A working mother can establish just as warm and secure a relationship with her children as a mother who does not work.		1840 (49.2)
972 (26.0)
610 (16.3)
213 (5.7)
52 (1.4)
55 (1.5)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesWomenWorkChildSuffer
A pre-school child is likely to suffer if his or her mother works.		424 (11.3)
1002 (26.8)
1112 (29.7)
730 (19.5)
414 (11.1)
60 (1.6)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesWomenWorkFamilySuffer
All in all, family life suffers when the woman is working.		150 (4.0)
568 (15.2)
1377 (36.8)
993 (26.5)
596 (15.9)
58 (1.6)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesHousewifeFulfilling
Being a housewife is just as fulfilling as working for pay.		520 (13.9)
622 (16.6)
1089 (29.1)
1013 (27.1)
430 (11.5)
68 (1.8)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesHousehusbandFulfilling
Being a househusband is just as fulfilling as working for pay.		318 (8.5)
468 (12.5)
1045 (27.9)
1208 (32.3)
579 (15.5)
124 (3.3)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesSingleParentEqual
One parent can raise a child as well as two parents together.		377 (10.1)
633 (16.9)
1181 (31.6)
1139 (30.4)
363 (9.7)
49 (1.3)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
SGRolesSameSexEqual
A same-sex couple can raise a child as well as a male-female couple.		667 (17.8)
838 (22.4)
898 (24.0)
708 (18.9)
567 (15.2)
64 (1.7)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
Externalized sex/gender expressions
SGExpressionLooks
How would other people generally describe you based on your appearance, clothing style and other visual characteristics?		413 (11.0)
884 (23.6)
256 (6.8)
326 (8.7)
253 (6.8)
1012 (27.0)
388 (10.4)
210 (5.6)		 = very masculine
= mainly masculine
= a little masculine
= just as feminine as masculine
= a little feminine
= mainly feminine
= very feminine
= missing
SGExpressionBehavior
How would other people generally describe you based on your behaviors?		384 (10.3)
876 (23.4)
301 (8.0)
455 (12.2)
232 (6.2)
953 (25.5)
338 (9.0)
203 (5.4)		 = very masculine
= mainly masculine
= a little masculine
= just as feminine as masculine
= a little feminine
= mainly feminine
= very feminine
= missing
SGExpressionSAGE
Combination of SexAtBirth,
SGExpressionLooks and
SGExpressionBehavior
SAGE-Score values: 1.0–7.0
low values = high socially assigned gender conformity
high values = low socially assigned gender conformity		876 (23.4)
1767 (47.2)
508 (13.6)
303 (8.1)
43 (1.2)
5 (0.1)
4 (0.1)
236 (6.3)
 = 1.0–1.5
= 2.0–2.5
= 3.0–3.5
= 4.0–4.5
= 5.0–5.5
= 6.0–6.5
= 7.0
= missing
Items contributing to explain structural sex/gender relations
Experience of discrimination
DiscriminationSocialPosition
I have the feeling to be disadvantaged because of my position in society.		40 (1.1)
202 (5.4)
354 (9.5)
1379 (36.9)
1717 (45.9)
50 (1.3)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationAge
I have the feeling to be disadvantaged because of my age.		49 (1.3)
251 (6.7)
431 (11.5)
1343 (35.9)
1630 (43.6)
38 (1.0)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationHeight
I have the feeling to be disadvantaged because of my height.		23 (0.6)
71 (1.9)
143 (3.8)
922 (24.6)
2544 (68.0)
39 (1.0)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationWeight
I have the feeling to be disadvantaged because of my weight.		29 (0.8)
75 (2.0)
187 (5.0)
888 (23.7)
2521 (67.4)
42 (1.1)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationDisability
I have the feeling to be disadvantaged because of my physical impairment.		46 (1.2)
95 (2.5)
228 (6.1)
644 (17.2)
2681 (71.7)
48 (1.3)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationEthnicity
I have the feeling to be disadvantaged because of my ethnic/cultural affiliation.		14 (0.4)
25 (0.7)
56 (1.5)
408 (10.9)
3185 (85.1)
54 (1.4)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationSG
I have the feeling to be disadvantaged because of my sex/gender.		17 (0.5)
42 (1.1)
128 (3.4)
495 (13.2)
3018 (80.7)
42 (1.1)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationSexualOrientation
I have the feeling to be disadvantaged because of my sexual orientation.		13 (0.4)
6 (0.2)
25 (0.7)
251 (6.7)
3368 (90.0)
79 (2.1)		 = strongly agree
= rather agree
= neither agree nor disagree
= rather disagree
= strongly disagree
= missing
DiscriminationAskedifParentsBornAbroad
Have you ever been asked in Germany whether you or your parents were born abroad?		415 (11.1)
3280 (87.7)
47 (1.3)		 = yes
= no
= missing
Care activities
CareActivitiesChildren
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Care and/or upbringing of your children/grandchildren, driving services for your children/grandchildren		155 (4.1)
329 (8.8)
1173 (31.4)
393 (10.5)
71 (1.9)
1572 (42.0)
49 (1.3)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= not applicable
= missing
CareActivitiesSick
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Care for disabled, chronically ill or in need of care family members, neighbors or friends		166 (4.4)
275 (7.4)
571 (15.3)
247 (6.6)
77 (2.1)
2342 (62.6)
64 (1.7)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= not applicable
= missing
CareActivitiesCooking
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Cooking		1049 (28.0)
756 (20.2)
877 (23.4)
650 (17.4)
348 (9.3)
62 (1.7)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= missing
CareActivitiesHousework
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Housework		896 (23.9)
877 (23.4)
1200 (32.1)
629 (16.8)
98 (2.6)
42 (1.1)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= missing
CareActivitiesGardening
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Gardening (during the gardening season)		495 (13.2)
686 (18.3)
1449 (38.7)
423 (11.3)
111 (3.0)
535 (14.3)
43 (1.2)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= not applicable
= missing
CareActivitiesErrands
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Errands (shopping, procurement)		797 (21.3)
800 (21.4)
1566 (41.9)
434 (11.6)
76 (2.0)
69 (1.8)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= missing
CareActivitiesAdministrativeTasks
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Administrative tasks (insurance, tax return, etc.)		1001 (26.8)
857 (22.9)
1191 (31.8)
481 (12.9)
163 (4.4)
49 (1.3)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= missing
CareActivitiesHandicraft
Who is currently taking primary responsibility for the following tasks?
(“Other people” also includes your partner)
Handicraft tasks in the household		704 (18.8)
936 (25.0)
906 (24.2)
850 (22.7)
303 (8.1)
43 (1.2)		 = only me
= mainly me
= me and other people
= mainly other people
= only other people
= missing
Intersectionality-related social categories
SGRelationsSchoolEducation
School education
(Variable from basic KORA studies S1–S4)		1736 (46.4)
 
1085 (29.0)
920 (24.6)
1 (0.03)		 = Degree after German basic secondary school (Hauptschulabschluss)
= German O-levels (Mittlere Reife)
= German A-Levels (Abitur)
= missing
SGRelationsVocationalEducation
Highest vocational qualification
(Variable from basic KORA studies S1-S4)		272 (7.3)
2064 (55.2)
725 (19.4)
32 (0.9)
648 (17.3)
1 (0.03)		 = no vocational qualification
= vocational school/apprenticeship
= technical school/master school
= engineering school/polytechnical school
= university of applied sciences/university
= missing
SGRelationsEmployment
Are you employed?
If so: How many hours do you work on average per week (actual working hours)?		1970 (52.7)
22 (0.6)
132 (3.5)
218 (5.8)
249 (6.7)
642 (17.2)
323 (8.6)
95 (2.5)
91 (2.4)		 = no
= 1–5 h/week
= 6–10 h/week
= 11–20 h/week
= 21–30 h/week
= 31–40 h/week
= 41–50 h/week
= >50 h/week
= missing
SGRelationsIncome
How do you assess your financial situation?		394 (10.5)
2303 (61.5)
937 (25.0)
66 (1.8)
42 (1.1)		 = very good
= good
= moderate
= bad
= missing
SGRelationsFamilySituation
Do you live with a spouse or partner in a shared household?
(Variable from KORA surveys F3, F4, FF4, FIT; the most recent available information from each participant was used)		2877 (76.9)
757 (20.2)
108 (2.9)		 = yes
= no
= missing
SGRelationsUrbanisation
Distribution of participants by degree of urbanisation.		1139 (30.4)
1392 (37.2)
751 (20.1)
460 (12.3)		 = city
= suburb
= rural
= missing
* Original questions were asked in German. # Percentages are calculated with respect to the whole sample, as participants with missing values in covariates are not excluded in the analysis.
Table
Table 2. Exposure distribution within the INGER sample.
Table 2. Exposure distribution within the INGER sample.
Exposure and, if Applicable, Questions * in INGER KORA SurveyAnswer Categories and Distribution
in the Whole INGER Study Sample;
N = 3742 (100%)
Subjective exposure measurement
Access to public green spaces
Are there publicly accessible green spaces (e.g., parks, forests, meadows) in your neighbourhood?		3383 (90.4) = yes
334 (8.9) = no
25 (0.7) = missing
Access to high quality public green spaces
The green spaces in my neighbourhood are well maintained.
The green spaces in my neighbourhood are of high quality.
(Combination of three variables)		1066 (28.5) = high quality green
2179 (58.2)
334 (8.9)
163 (4.4)		 = only lower quality green
= no green
= missing
Greenness in the neighbourhood
How green is your neighbourhood?
(From green strips along the road to gardens and parks.)		2911 (77.8) = very green
731 (19.5) = little green
78 (2.1) = hardly green
22 (0.6) = missing
Objective exposure measurement
Greenness within a 300 m buffer around the residential address
Calculated from several satellite images between April and October in 2019. Negative pixels of the NDVI map were excluded prior to assignment to home addresses.		0.16
0.41
0.47
0.47
0.09
0.53
0.73
N = 11		 = min
= Q1
= median
= mean
= SD
= Q3
= max
missing
Greenness within a 1000 m buffer around the residential address
Calculated from several satellite images between April and October in 2019. Negative pixels of the NDVI map were excluded prior to assignment to home addresses.		0.27 = min
0.44
0.50
0.50
0.09
0.57
0.71
N = 11		 = Q1
= median
= mean
= SD
= Q3
= max
missing
* Original questions were asked in German.
Table
Table 3. Further description of the INGER study population.
Table 3. Further description of the INGER study population.
Question * In INGER KORA SurveyAnswer Categories and Distribution in the Whole Sample;
N = 3742 (100%)
Age distribution in the INGER study population.Continuous variable (years)
63.41 = mean
9.42
43.00
92.00
0		 = SD
= min
= max
= missing
What is your current employment status?1681 (44.9)
1786 (47.7)
184 (4.9)
91 (2.4)		 = employed
= retired
= other
= missing
Do you live…?2951 (78.9)
759 (20.3)
32 (0.9)		 = in your own property
= for rent
= missing
How long have you lived at your current address?Continuous variable
29 years
16.31
0
93
68		 (years)
= mean
= SD
= min
= max
= missing
How often do you usually reside at your current address?3655 (97.7)
19 (0.5)
25 (0.7)
17 (0.5)
26 (0.7)		 = daily
= only on weekdays
= only on days off
= few days a month
= missing
Does your flat or house have a garden?2614 (69.9)
362 (9.7)
723 (19.3)
43 (1.2)		 = yes, for sole use
= yes, shared with several parties
= no
= missing
Do you have a balcony and/or terrace?2684 (71.7)
985 (26.3)
73 (2.0)		 = yes
= no
= missing
Do you use your garden, balcony or terrace for recreation?3359 (89.8)
287 (7.7)
63 (1.7)
33 (0.9)		 = yes
= no
= neither garden, balcony nor terrace available
= missing
During the summer months, how often do you visit publicly accessible green spaces, such as…
 
… parks, forests, meadows, which you can reach in about 10 min?		289 (7.7)
283 (7.6)
264 (7.1)
528 (14.1)
1146 (30.6)
794 (21.2)
334 (8.9)
104 (2.8)		 = (almost) never
= 3–6 times per year
= 7–10 times per year
= at least once a month
= at least once a week
= (almost) daily
= no publicly accessible green spaces available
= missing
During the summer months, how often do you visit publicly accessible green spaces, such as…
 
… parks, forests, meadows, which you cannot reach in about 10 min?		569 (15.2)
539 (14.4)
473 (12.6)
792 (21.2)
692 (18.5)
144 (3.9)
334 (8.9)
199 (5.3)		 = (almost) never
= 3–6 times per year
= 7–10 times per year
= at least once a month
= at least once a week
= (almost) daily
= no publicly accessible green spaces available
= missing
* Original questions were asked in German.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Dandolo, L.; Hartig, C.; Telkmann, K.; Horstmann, S.; Schwettmann, L.; Selsam, P.; Schneider, A.; Bolte, G.; on behalf of the INGER Study Group. Decision Tree Analyses to Explore the Relevance of Multiple Sex/Gender Dimensions for the Exposure to Green Spaces: Results from the KORA INGER Study. Int. J. Environ. Res. Public Health 2022, 19, 7476. https://doi.org/10.3390/ijerph19127476

AMA Style

Dandolo L, Hartig C, Telkmann K, Horstmann S, Schwettmann L, Selsam P, Schneider A, Bolte G, on behalf of the INGER Study Group. Decision Tree Analyses to Explore the Relevance of Multiple Sex/Gender Dimensions for the Exposure to Green Spaces: Results from the KORA INGER Study. International Journal of Environmental Research and Public Health. 2022; 19(12):7476. https://doi.org/10.3390/ijerph19127476

Chicago/Turabian Style

Dandolo, Lisa, Christina Hartig, Klaus Telkmann, Sophie Horstmann, Lars Schwettmann, Peter Selsam, Alexandra Schneider, Gabriele Bolte, and on behalf of the INGER Study Group. 2022. "Decision Tree Analyses to Explore the Relevance of Multiple Sex/Gender Dimensions for the Exposure to Green Spaces: Results from the KORA INGER Study" International Journal of Environmental Research and Public Health 19, no. 12: 7476. https://doi.org/10.3390/ijerph19127476

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop