- 1Florida Institute for Built Environment Resilience, College of Design, Construction and Planning, University of Florida, Gainesville, FL, United States
- 2School for Environment and Sustainability, University of Michigan, Ann Arbor, MI, United States
- 3Institute for Social Research, University of Michigan, Ann Arbor, MI, United States
- 4Department of Psychology, University of Michigan, Ann Arbor, MI, United States
- 5Graduate School of Social Work, University of Denver, Denver, CO, United States
Understanding community members' flood risk perceptions is critical for developing new approaches to managing flood risks for climate resilience. “Risk as feelings” has informed research on how people perceive flood risks based on intuition and personal experiences, complementing experts' technical assessment. However, attention has been primarily on riverine and coastal flooding. We expand the “risk as feelings” concept to investigate community members' risk perceptions of urban pluvial flooding as well as perceived safety of novel vs. familiar nature-based solutions (NBS). For the novel practice, we focus on floodable sites that temporarily inundate urban open spaces under storm conditions. For the familiar practice, we focus on retention ponds that store excessive runoff under storm conditions. Data were collected through visualization-assisted surveys of residents from high and low flood hazard areas in three US cities (N = 884). We found that over half of respondents indicated some degree of worry about stormwater-related damage, and overall, respondents perceived floodable as less safe than retention ponds under storm conditions. Further, respondents who had more frequently experienced localized flooding near their homes were more worried about potential property damage caused by flooding. They also perceived floodable sites as less safe under storm conditions. However, more frequent experience of localized flooding was not associated with perceived safety of retention ponds under storm conditions. Some other contextual and socio-demographic factors (e.g., prior stormwater-related property damage, knowledge of and involvement in stormwater management issues, gender, age, race, and having children) also had notable effects on flood risk perception and perceived safety of NBS. We discuss the implications of these findings for urban flood risk management and NBS development.
Introduction
Climate change, coupled with urban development and aging infrastructure, is driving more pluvial flooding in cities (Berndtsson et al., 2019; National Academies of Sciences Engineering and Medicine, 2019; O'donnell and Thorne, 2020). The management of urban stormwater and flooding risks increasingly aims for resilience, the capacity to absorb, recover from, and adapt to extreme storm events and their uncertain impacts (Liao, 2012; Disse et al., 2020; Mcclymont et al., 2020). Such a shift calls for changes in urban landscapes to make space for water, and many government agencies and organizations are developing nature-based solutions (NBS) as a promising approach (Hobbie and Grimm, 2020; Axelsson et al., 2021). NBS include various practices (e.g., retention ponds, detention swales and basins, constructed wetlands) that seek to use natural processes to manage stormwater and mitigate flooding while offering other societal benefits (Lennon et al., 2014; Hobbie and Grimm, 2020; O'donnell et al., 2020).
One increasingly discussed NBS innovation is floodable sites, urban spaces designed to accommodate different dry and wet weather functions (Palazzo, 2019; Ashley et al., 2020; Kuang and Liao, 2020; La Loggia et al., 2020). In dry weather, they are used for everyday activities (e.g., recreation, parking, light traffic); in wet weather, they are temporarily inundated to manage excessive storm runoff and mitigate flooding (Mariano and Marino, 2018; Silva and Costa, 2018; Lund et al., 2019; Rogers et al., 2020). Floodable sites can include diverse types of urban spaces for stormwater and flood risks management. Some scholars have also argued that introducing such practices may help urban residents observe and learn about stormwater, thus encouraging a shift in social-cultural norms to “live with water” (Lennon et al., 2014; Silva and Costa, 2018; Kuang and Liao, 2020; Mcclymont et al., 2020).
However, scant research exists on how community members perceive novel NBS practices like floodable sites. There are anecdotes of residents calling a water plaza designed as a floodable site a “drowning plaza” (Silva and Costa, 2018). In cities, drainage systems have long been adopted to discourage standing water, treating stormwater as a nuisance that can disturb daily activities (Tempels and Hartmann, 2014; Ashley et al., 2020; Kuang and Liao, 2020). The visible ponding and puddling in typically dry floodable sites might feel unpleasant and unsafe to urban residents. This can undermine public acceptance of novel NBS practices despite their environmental benefits (Derkzen et al., 2017; Frantzeskaki, 2019; Han and Kuhlicke, 2019; Anderson and Renaud, 2021; Li and Nassauer, 2021).
To offer new insights for managing urban flooding through NBS, this study uses “risk as feelings” as an organizing framework to investigate community members' risk perceptions. This concept is embedded in a broader theory in cognitive psychology and neuroscience which asserts that humans use both affective and cognitive processing—a “dual process” model—to comprehend the world (Loewenstein et al., 2001; Slovic et al., 2004). Affective processing, which occurs when people perceive something as good or bad, is often labeled experiential, intuitive, and automatic; cognitive processing, which occurs when people use explicit reasoning, is often labeled analytical and deliberative (Epstein, 1994; Kahneman, 2011). Both processes are now recognized as critical to decision-making. When faced with risk or uncertainty, though, people are prone to make judgements driven by how they feel about an outcome rather than by deliberation about its probability and consequences (Slovic, 1987; Slovic et al., 1998; Disse et al., 2020). For example, if people have unfavorable feelings toward using pesticides, they tend to perceive high risk and low benefit of pesticides; if they have favorable feelings, they tend to perceive the opposite (Alhakami and Slovic, 1994). The risk perception of a phenomenon can be strongly affected by past experiences of the same phenomenon or one with similar perceptible characteristics (Loewenstein et al., 2001). Through lived experience and learning, certain sights, sounds, smells, ideas, and words can become associated with positive and negative feelings, forming “affective images” that guide responses in future situations (Slovic et al., 1998).
“Risk as feelings” has informed many studies on flood risk perception—the perceived likelihood and potential damage of flooding (Botzen et al., 2009; Kellens et al., 2013; Wachinger et al., 2013; Birkholz et al., 2014; O'neill et al., 2016; Lechowska, 2018). Flood risk perception often differs from expert technical assessments of flood risks and is consistently reported to relate to past experiences of flooding (Botzen et al., 2009; Kellens et al., 2013; Wachinger et al., 2013; Birkholz et al., 2014; O'neill et al., 2016; Lechowska, 2018). For example, Botzen et al. (2009) found that individuals who had experienced or been evacuated from a historic flood event in the Netherlands reported a higher perceived probability of flooding. Besides flood experience, socio-demographic characteristics (e.g., age, gender, income, education, having young children) may also influence flood risk perception, though their reported effects are not consistent (Kellens et al., 2013; Wachinger et al., 2013; Lechowska, 2018). For example, some studies found that people with higher education perceived lower flood risks (Botzen et al., 2009; Bradford et al., 2012), whereas other studies reported no association betweeen eduction and risk perception (Kellens et al., 2011; O'neill et al., 2016).
While the growing literature on flood risk perception provides important insights for flood risk communication and management, most studies have focused on major riverine and coastal flooding. Urban pluvial flooding, which results from overwhelmed drainage systems and occurs more frequently, calls for more investigation (Netzel et al., 2021). Further, risk perception related to novel NBS that are designed to manage urban pluvial flooding has not yet been examined, to our knowledge.
This study investigates the risk perception of localized flooding and the perceived safety of novel and familiar NBS practices. We examine how people with different past experiences with localized flooding perceive the risk of urban pluvial flooding as well as the perceived safety of novel and familiar NBS under storm conditions. We compare perceptions of floodable sites, a novel NBS practice that temporarily inundates urban landscapes under the storm condition, with perceptions of stormwater retention ponds, a familiar NBS practice that can hold excess water under the storm condition. We also explore whether other contextual (e.g., residence location relative to flood zone, environmental knowledge) and socio-demographic factors are associated with perceived flood risk and perceived safety of NBS practices. Specifically, we address four questions:
1) What are community members' perceptions of localized flooding risks?
2) How safe are floodable sites (a novel NBS) and retention ponds (a familiar NBS) perceived to be under storm conditions? Are floodable sites perceived as less safe than retention ponds?
3) Are community members' flood risk perception and perceived safety of NBS practices under storm conditions associated with their experience of localized flooding?
4) What other contextual and socio-demographic factors may relate to community members' flood risk perception and perceived safety of NBS practices under storm conditions?
Materials and methods
Study area
We conducted a mail survey in three US cities: Ann Arbor, Michigan, South Bend, Indiana, and Knoxville, Tennessee (Figure 1). All three cities have experienced severe urban flooding within the past 4 years. Further, with climate change, these cities all face growing flood risks. Projections by the First Street Foundation (2022) based on factors including flood hazards, property and parcel conditions, future climate scenarios, and local adaptation predict that, for the next 30 years, Ann Arbor has a moderate risk of flooding, with 4% of properties having over a 26% chance of being severely affected by flooding. South Bend and Knoxville have a major risk of flooding, with 11% of properties having over a 26% chance of being severely affected by flooding.
Sampling method
To include respondents with potentially varied experiences of flooding, we used a stratified random sampling method to recruit respondents for our survey. First, we categorized census blocks in each city into four strata, considering combinations of low/high flood hazards and low/high income. High vs. low flood hazards was based on whether a census block intersected with the Special Flood Hazard Area (100-year flood) and the moderate flood hazard areas (500-year flood) designated by the US Federal Emergency Management Agency (FEMA) (https://msc.fema.gov/portal/home). High vs. low income of a block was based on the income of the block group it was in. Census block groups with median household income higher than the city's median household income were designated as high income, while census block groups with median household income lower than the city's median household income were designated as low income. We excluded census block groups with a median age under 25 to avoid recruiting substantial numbers of students who are temporary residents living near universities in each city.
Next, we randomly selected 336 household addresses within each of the 12 strata (3 cities × 2 income levels × 2 flood hazard levels) to receive the survey invitation, resulting in a mail sample of a total of 4,032 household addresses. This sample size was estimated to be sufficient to yield a minimum of 200 completed surveys per city based on requirements for structural equation modeling (Kline, 2015) and an estimated response rate of 15% given previous studies on green infrastructure that also used a mail survey (Ambrey et al., 2017; Williams et al., 2019).
Survey design
Landscape visualizations to represent NBS practices
For survey respondents to see novel and familiar NBS practices under storm conditions, we developed landscape visualizations of floodable sites and stormwater retention ponds. Visualizations are widely used to study visual perception of landscapes (Jorgensen et al., 2002; Sevenant and Antrop, 2011). Moreover, realistic visual imagery may help ground information, broaden respondents' experiences, and facilitate understanding of new landscape futures (Sheppard, 2005). This is particularly useful for representing novel NBS, such as floodable sites that are unfamiliar to the general public.
Our team manipulated photos of 10 potential sites for NBS development in the three study cities in Adobe Photoshop CC to create 34 sets of visualizations. Each visualization set realistically depicted a floodable site or a retention pond under both storm and non-storm conditions (Figure 2). Floodable sites were shown as both dry non-storm conditions and inundated storm conditions in two locations (i.e., basketball courts in greenspace and parking lots around building complexes), with two replicate sites for each location. Retention ponds were shown at both typical water level non-storm conditions and high water-level storm conditions with 15 landscape design choices (varied by types of surrounding plants, basin slope, and land use context), with two replicate sites for each design choice.
Figure 2. Examples of visualizations for floodable sites, a novel NBS practice, and retention ponds, a familiar practice, under storm and non-storm conditions. Image credit: The Landscape Ecology, Perception, and Design Lab, University of Michigan (https://www.joan-nassauer.com/).
Questionnaire
The survey questionnaire consisted of two parts. The first part showed visualizations for retention ponds and floodable sites under storm and non-storm conditions. For each NBS practice, visualizations were color-printed in high resolution (8.3 × 12.5 cm) and laid out on a single page to show different storm conditions. There was a short description of the site for stormwater management practice that respondents were seeing (e.g., “This is a basketball court. It holds water only temporarily, after a storm.”). Respondents were asked about their perceptions of how safe each picture looked on a 5-point Likert scale. The second part of the questionnaire asked respondents about their experiences with flooding, worry about potential damages caused by stormwater, knowledge and behaviors related to general environmental and stormwater issues, and socio-demographic characteristics. Section 2.4 further explains questionnaire items that were used as measures in this study.
To avoid attention fatigue from seeing all 34 sets of visualizations for NBS practices, we created eight versions of questionnaires. Each version included five retention ponds selected from the 30 options and randomly ordered, followed by one floodable site selected from the four options. Within each of the 12 respondent sampling strata, all eight versions of the questionnaire were randomly assigned to household addresses.
Survey procedure
We administered the survey via the US postal mail in 2019, with approval by the University of Michigan Institutional Review Board. To increase the response rate, we first introduced the project and upcoming survey to the selected households by postcard. Next, we mailed the questionnaire with an explanatory letter, an informed consent document, a pre-paid return envelope, and a $1 pre-incentive. The letter provided information about the survey and invited a household member at least 18 years old to participate. A US $10 token of appreciation was offered to respondents who completed and returned the survey.
Measures
To address our first research question, we operationalized flood risk perception by asking respondents to rate how much they would worry about potential damages to their home or property when noticing standing water caused by water from rain or melting snow near home. We used a 4-point Likert scale (Do not worry at all = 1, Worry a little = 2, Worry some = 3, Worry a lot = 4). This is similar to how some previous studies measured flood risk perception (Kellens et al., 2013; O'neill et al., 2016).
To address our second research question, we operationalized perceived safety of NBS practices under storm conditions by respondents' ratings on how safe the visualizations they saw on a 5-point Likert scale (Dangerous = 1, Somewhat dangerous = 2, Neither = 3, Somewhat safe = 4, Safe = 5). Specifically, perceived safety of floodable sites used the rating of the single site that each respondent viewed whereas perceived safety of retention ponds was based on the average rating across the five retention ponds that each respondent viewed (Cronbach's alpha = 0.86).
To address our third question about the impact of flood experience, we operationalized experience of localized flooding by the frequency of noticing flooding or standing water in locations near one's home in the past 2 years when there was rain or snow melting. We used a 4-point Likert scale (Never = 1, Sometimes = 2, Often = 3, Always = 4) and averaged ratings across five locations near each respondent's home (i.e., home driveway, home yard, neighbor's property, street, and nearby block) for a composite measure (Cronbach's alpha = 0.81).
To address our fourth research question, we considered some contextual and socio-demographic factors as explanatory variables (Table 1). Based on previous studies, we included variables related to flooding-induced damage (Kellens et al., 2013; Lechowska, 2021) and residence location (Botzen et al., 2009; O'neill et al., 2016). We also included variables related to environmental knowledge and behavior, which may affect perceptions of NBS (Feng and Nassauer, 2022). We examined socio-demographic factors of age, gender, race, education, and household income based on reviews of research on flood risk perception (Kellens et al., 2013; Wachinger et al., 2013; Lechowska, 2021) and reviews of research on public perception of NBS (Flotemersch and Aho, 2021; Feng and Nassauer, 2022). We also examined whether respondents had young children in their household given that perceived safety of NBS practices can relate to concerns about drowning hazards (Bastien et al., 2012; Jarvie et al., 2017; Williams et al., 2019).
Table 1. Explanatory variables related to contextual and socio-demographic factors and their measurement scales.
Data analysis
The overall survey response rate was 24.2% (974/4,032). For this study, we excluded respondents who did not provide information on their addresses or reported addresses outside our sampling area. We used the resulting sample (N = 884) in subsequent data analysis, which was conducted in R 4.0.2 (R Core Team, 2020).
To address our first research question, we calculated descriptive statistics for the extent of worry about potential stormwater-related damages to home or property among respondents. To address our second research question, we calculated descriptive statistics for perceived safety of both NBS practices under storm and non-storm conditions, followed by inferential statistics to compare the mean ratings for perceived safety of floodable sites and retention ponds using t-test.
To address the third and fourth research questions, we conducted multiple linear regression analysis to examine the effects of experience of localized flooding, as well as other contextual and socio-demographic factors on (1) flood risk perception, (2) perceived safety of floodable sites under storm conditions, and (3) perceived safety of retention ponds under storm conditions, using p-value < 0.05 as the threshold of significance. To model perceived safety of floodable sites and retention ponds under storm conditions, we controlled for perceived safety under non-storm conditions for both NBS practices. We then calculated the unstandardized (b) and standardized (β) coefficients for each of the three models.
Results
Survey respondents' socio-demographic profile, experience of localized flooding, and other contextual characteristics
The socio-demographic characteristics of the 884 survey respondents were similar to the characteristics of the study area population (Table 2). Our sample had slightly fewer people of age 18–44 and more people of age 65 and above. Also, it was slightly higher in the percentage of female, and slightly lower in the percentage of non-white and less than high school education.
461 among the 884 respondents (52.1%) were from census blocks identified with high flood hazards in our sampling frame (Table 3). This confirmed that the sampling of survey respondents in low vs. high flood hazard areas was well-balanced. Respondents reported a mean frequency of 1.93 out of 4 that they had noticed standing water in locations near their home in the past 2 years (with Never = 1, Sometimes = 2, Often = 3, Always = 4). Over one fifth of respondents also had stormwater-related property damage in the past 2 years. However, only 4.5% of the respondents identified themselves as living in an officially designated flood zone. We therefore excluded “perceived home location relative to flood zone” as an explanatory variable in further data analysis due to its low variability.
Risk perception of urban pluvial flooding and perceived safety of NBS practices
RQ1: What are community members' perceptions of localized flooding risks?
The majority (66.0%) of respondents worried at least a little about potential property damage when noticing standing water or flooding near their home (Table 4).
Table 4. Respondents' flood risk perception. Measured by their indicated level of worry about potential property damage when they noticed standing water or flooding near home.
RQ2: How safe are floodable sites and retention ponds perceived to be under storm conditions? Are floodable sites perceived as less safe than retention ponds?
Comparing storm vs. non-storm conditions, perceived safety was lower under storm conditions for both floodable sites and retention ponds (Table 5). Floodable sites were perceived as significantly less safe under storm conditions than under non-storm conditions (paired t-test, 95% CI [−1.79, −1.60], p < 0.001). Retention ponds were also perceived as significantly less safe when under storm conditions than under non-storm conditions (paired t-test, 95% CI [−1.10, −0.97], p < 0.001).
Table 5. Mean scores (SD) for perceived safety of different NBS practices under storm and non-storm conditions.
Comparing floodable sites and retention ponds, under non-storm conditions, floodable sites were perceived as significantly safer than retention ponds (paired t-test, 95% CI [−0.39, −0.22], p < 0.000). In contrast, under storm conditions, floodable sites were perceived as significantly less safe than retention ponds (paired t-test, 95% CI [0.26, 0.45], p < 0.001).
RQ3: Are community members' flood risk perception and perceived safety of NBS practices under storm conditions associated with their experience of localized flooding?
Respondents who more frequently noticed standing water or flooding near their homes indicated significantly greater worry about potential damages caused by stormwater (Table 6). They also perceived floodable sites under storm conditions as significantly less safe. In contrast, experience of localized flooding showed no significant effect on perceived safety of retention ponds under storm conditions.
Table 6. Results from multiple linear regression models for (a) flood risk perception, (b) perceived safety of floodable sites under storm conditions, controlling for perceived safety under non-storm conditions, and (c) perceived safety of retention ponds under storm conditions, controlling for perceived safety under non-storm conditions.
RQ4: What other contextual and socio-demographic factors may relate to community members' flood risk perception and perceived safety of NBS practices under storm conditions?
Respondents who had stormwater-related property damage in the past 2 years, participated in activities addressing stormwater management issues in the past 2 years, or knew more about local water quality, indicated significantly greater worry about potential stormwater-related damage to home or property (Table 6a). Female respondents also indicated significantly greater worry. In contrast, respondents who participated in activities to promote general environmental sustainability in the past 2 years indicated significantly less worry than those who did not participate in such activities.
Regarding perceived safety of NBS practices, respondents who were female or lived in high flood hazard areas perceived floodable sites under storm conditions to be significantly less safe (Table 6b). Respondents who were female, non-white, or with children under the age of 12 in their households perceived retention ponds under storm conditions to be significantly less safe, whereas older respondents perceived retention ponds under storm conditions to be significantly safer (Table 6c).
Discussion
This study aims to inform resilient approaches to urban flood risks and stormwater management that can better respond to growing extreme weather events under climate change. We investigated community members' risk perception of urban pluvial flooding and perceived safety of NBS practices, using “risk as feelings” to frame our research questions. To shed light on how perceived safety may vary by different design solutions for storing stormwater, we compared two types of practices: floodable sites, a novel NBS practice that temporarily inundates urban landscapes, and stormwater retention ponds, a familiar NBS practice that always has water. We also examined how flood risk perceptions and perceived safety of NBS practices are associated with experiences of localized flooding, as well as other contextual and socio-demographic factors.
The majority of our study respondents indicated some degree of worry about potential damage to property when noticing standing water near home. This result is somewhat expected. Recent studies have reported that community members are generally aware of urban flooding problems (Derkzen et al., 2017; Meerow et al., 2021). Regarding the question of perceived safety of NBS practices, this study indicates that community members may perceive NBS practices that visibly change stormwater levels in surrounding landscapes as unsafe. Both floodable sites and retention ponds were perceived as less safe under storm conditions than under non-storm conditions. Furthermore, ponds were perceived as safer than floodable sites under storm conditions. Reflecting on these results through the “risk as feelings” framework, we speculate that people might intuitively perceive inundated floodable sites that look like flooding events as less safe, whereas water level fluctuations in retention ponds are more expected because it is a natural-looking practice where water is typically present. While we did not directly measure feelings (e.g., through a psychometric paradigm or physiological change), our study provides a basis for future research to examine affective reactions to novel and familiar NBS practices that have noticeable water level changes. We also call for more research on why people view water level changes as unsafe and what influences such perceptions might have on well-being or support for the adoption of NBS practices.
Prior studies have shown associations between personal experiences of major riverine and coastal flooding and greater perceived risks and discussed how witnessing disastrous events may help people envision low-probability events and their consequences (Botzen et al., 2009; Kellens et al., 2011; O'neill et al., 2016). Importantly, we found that the experience of less intense localized events—seeing standing water and flooding near home—are also associated with greater flood risk perception. As “risk as feelings” implies, intuitive perceptions of risks involve affective processing and do not always reflect the actual magnitude of damage. Further, experience of localized flooding may also undermine perceived safety of floodable sites under storm conditions. However, we found no associations between such experience and perceived safety of retention ponds under storm conditions. This has important implications for stormwater management interventions that are more likely to gain support in communities having experienced localized flooding.
We also found notable effects of other contextual and socio-demographic factors on the risk perception of urban pluvial flooding and the perceived safety of NBS practices. Consistent with research focused on riverine and coastal flooding (Kellens et al., 2013; Lechowska, 2021), we also observed strong associations between gender (female) as well as past property damage and greater perceived risks of localized flooding. Different from previous studies (Botzen et al., 2009; Kellens et al., 2013), we did not find associations between higher education level and lower flood risk perception. However, our results suggest more nuanced effects of knowledge and behavior specifically related to stormwater. In this study, respondents who indicated more knowledge about local water quality or had participated in activities addressing stormwater management issues (i.e., wrote a letter or made a phone call, attended or arranged a public meeting, or talked to a manager face to face) in the past 2 years were more worried about potential stormwater-related damage. In contrast, respondents who had participated in activities promoting general environmental sustainability (i.e., made donations, volunteered or served in a leadership positions for an organization or advocacy group, voted for a candidate for public office) in the past 2 years were less worried about potential stormwater-related damage. Perhaps people who participate in activities to promote general sustainability are not necessarily interested in or well-informed about stormwater management and focus more on other environmental issues (e.g., greenhouse gas reduction, wildlife habitat). Research on flood risk perception should continue to investigate knowledge and behaviors related more specifically to stormwater and water systems to further understand their influences.
Perceived safety of floodable sites was associated with only one socio-demographic factor—gender, whereas perceived safety of retention ponds was associated with several socio-demographic factors. The lower perceived safety of both practices among female respondents might be attributed to social norms for males to not express worry (Sutton and Farrall, 2005). It might also relate to females' primary role in taking care of children and home. Future research may conduct more qualitative analyses of the potential gender differences in perceived safety of NBS practices for stormwater management. For retention ponds, respondents with children under the age of 12 in their households perceived retention ponds under storm conditions as less safe. This reflects concerns about drowning hazards and personal safety, especially for children, that have been observed in previous studies (Bastien et al., 2012; Jarvie et al., 2017; Williams et al., 2019). Moreover, non-white respondents perceived retention ponds as less safe, while older respondents perceived retention ponds as safer. People of color may have less experience with well-maintained retention ponds given their often more limited access to high-quality, large greenspace (Rigolon, 2016). Older people may have more contact with nature and thus are more familiar with the fluctuation between typical and high water levels. These results point to potentially different causes that shape perceived safety of floodable sites and stormwater ponds under storm conditions.
Further, the adjusted R-squared for the perceived safety model of floodable sites (12.0%) is smaller than that for the model of retention ponds (39.0%), indicating a lower explanatory power. Therefore, factors besides the contextual and socio-demographic variables examined in this study, such as landscape design choices and environmental values, may impact the perceived safety of floodable sites, and more research is needed.
Implications for urban flood risk management and NBS development
This study has several implications for resilient urban flood risk management and NBS development. First, based on our finding on the widely present worry about potential stormwater-related damage and its association with experiences of localized flooding near home, we call for more attention to pluvial flooding in urban flood risk management. Urban pluvial flooding is less addressed than riverine and coastal flooding. This in part results from the lack of local data for fine-scale built environment characteristics such as stormwater infrastructure inadequacies and impervious surfaces that contribute to pluvial flooding (National Academies of Sciences Engineering and Medicine, 2019). Therefore, publicly available data are needed to more precisely map areas prone to pluvial flooding at the local scale and identify priorities for developing interventions to manage stormwater. Further, when NBS practices are proposed for stormwater management, their relevance to reducing flood risks should be more clearly communicated to the public (Derkzen et al., 2017).
Second, we caution that when developing NBS practices, local community members' perceptions should be considered in addition to stormwater management functions. Different from experts, community members may intuitively perceive NBS practices that introduce noticeable water level changes as unsafe, especially for novel practices like floodable sites. Based on our finding that floodable sites were perceived as less safe than retention ponds, we recommend that renovating familiar NBS practices (e.g., retention ponds) to increase their storage capacity may be preferable to developing novel NBS practices that temporarily inundate urban spaces (e.g., floodable sites). In intensely developed areas where floodable sites are more feasible or desirable, more research is needed to inform design guidelines that can help increase perceived safety. In this study, we treated floodable sites as a homogeneous category without accounting for variations in possible design choices. Additional studies are needed to understand how various types of floodable sites (e.g., parking lots, recreational sites, minor streets, blue roofs, parks, and urban plazas) and the frequency of inundation may affect perceived safety of floodable sites. Studies can also test whether communicating floodable sites' functions, for example, through signages, education programs, or demonstration of pilot sites, may improve perceived safety.
Further, engagement with local communities should anticipate that perceptions of NBS practices may vary by flood experience and socio-demographic groups. This study shows that females, people of color, and families with children are likely to have more safety concerns. However, we only examined individuals' perceptions and their associations with individual experiences of localized flooding and socio-demographic characteristics. Given that flooding often disproportionately affects underserved communities (National Academies of Sciences Engineering and Medicine, 2019; Eakin et al., 2022), more research is needed to understand whether and how communities with varied flood experiences and socio-demographic status may differ in perceptions of flood risks and NBS practices.
Conclusion
We assert that urban flood risk management should engage with social science theories such as “risk as feelings” to account for peoples' affective responses and intuitive perceptions. Drawing on the concept of “risk as feelings,” this paper deepens the understanding of how community members perceive urban pluvial flooding by highlighting the effects of experience of localized flooding and other contextual and socio-demographic factors. It also provides new insights into developing nature-based solutions (NBS) for managing urban stormwater by elucidating how noticeable stormwater level changes in novel and familiar NBS practices can elicit safety concerns. Notably, we found that, under storm conditions, floodable sites, a novel NBS practice that temporarily inundates urban spaces to manage stormwater, were perceived as less safe than retention ponds, a familiar NBS practice that always has water. Further, community members with more experiences of localized flooding perceived floodable sites as less safe, while those who were younger, non-white, or had children in their households perceived retention ponds as less safe. The difference in perceived safety of these two types of NBS practices have implications for public support for their adoption. We call for inter and trans-disciplinary collaborations in designing new landscape interventions to address extreme weather events and the increasing urban flood risks. Pervasive adoption of NBS must consider potential impacts on people's everyday experiences in their neighborhoods and communities, in addition to stormwater management objectives, to gain broad societal support.
Data availability statement
The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.
Ethics statement
The studies involving human participants were reviewed and approved by Institutional Review Boards, University of Michigan. The patients/participants provided their written informed consent to participate in this study.
Author contributions
JL: conceptualization, methodology, formal analysis, data curation, and writing—original draft preparation. JN: conceptualization, methodology, funding acquisition, supervision, and writing—review and editing. NW: methodology, investigation, funding acquisition, and writing—review and editing. SP: conceptualization, data interpretation, and writing—review and editing. LM: investigation, funding acquisition, and writing—review and editing. All authors contributed to the article and approved the submitted version.
Funding
This work was funded by the US National Science Foundation: SCC-IRF 1737432. Overcoming Social and Technical Barriers for the Broad Adoption of Smart Stormwater Systems. We are also grateful for funds received from the University of Florida that supports the open access publication of this paper.
Acknowledgments
We especially thank Yuanqiu Feng for leading development of visualizations employed in our questionnaire and the questionnaire layout. We thank student assistants in the University of Michigan Landscape Ecology Perception and Design Lab who assisted with visualizations: Alexis Heinz, Chuyi Yin, Jingyuan Wu, Neha Srinivasan, Soyoung Jin, Yanling Mo, Yanning Gao, and Yiran Shen. We also thank the two reviewers for their helpful feedback and comments.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher's note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
References
Alhakami, A. S., and Slovic, P. (1994). A psychological study of the inverse relationship between perceived risk and perceived benefit. Risk Anal. 14, 1085–1096.
Ambrey, C., Byrne, J., Matthews, T., Davison, A., Portanger, C., and Lo, A. (2017). Cultivating climate justice: green infrastructure and suburban disadvantage in Australia. Appl. Geogr. 89, 52–60. doi: 10.1016/j.apgeog.2017.10.002
Anderson, C. C., and Renaud, F. G. (2021). A review of public acceptance of nature-based solutions: the “why,” “when,” and “how” of success for disaster risk reduction measures. Ambio 50, 1552–1573. doi: 10.1007/s13280-021-01502-4
Ashley, R., Gersonius, B., and Horton, B. (2020). Managing flooding: from a problem to an opportunity. Philos. Trans. R. Soc. A 378, 20190214. doi: 10.1098/rsta.2019.0214
Axelsson, C., Soriani, S., Culligan, P., and Marcotullio, P. (2021). Urban policy adaptation toward managing increasing pluvial flooding events under climate change. J. Environ. Plann. Manag. 64, 1408–1427. doi: 10.1080/09640568.2020.1823346
Bastien, N. R. P., Arthur, S., and Mcloughlin, M. J. (2012). Valuing amenity: public perceptions of sustainable drainage systems ponds. Water Environ. J. 26, 19–29. doi: 10.1111/j.1747-6593.2011.00259.x
Berndtsson, R., Becker, P., Persson, A., Aspegren, H., Haghighatafshar, S., Jönsson, K., et al. (2019). Drivers of changing urban flood risk: a framework for action. J. Environ. Manag. 240, 47–56. doi: 10.1016/j.jenvman.2019.03.094
Birkholz, S., Muro, M., Jeffrey, P., and Smith, H. M. (2014). Rethinking the relationship between flood risk perception and flood management. Sci. Total Environ. 478, 12–20. doi: 10.1016/j.scitotenv.2014.01.061
Botzen, W. J., Aerts, J., and Van Den Bergh, J. C. (2009). Dependence of flood risk perceptions on socioeconomic and objective risk factors. Water Resour. Res. 45, 7743. doi: 10.1029/2009WR007743
Bradford, R. A., O'Sullivan, J. J., Van der Craats, I. M., Krywkow, J., Rotko, P., Aaltonen, J., et al. (2012). Risk perception—issues for flood management in Europe. Nat. Hazards Earth Syst. Sci. 12, 2299–2309. doi: 10.5194/nhess-12-2299-2012
Derkzen, M. L., Van Teeffelen, A. J., and Verburg, P. H. (2017). Green infrastructure for urban climate adaptation: how do residents' views on climate impacts and green infrastructure shape adaptation preferences? Landscape Urban Plann. 157, 106–130. doi: 10.1016/j.landurbplan.2016.05.027
Disse, M., Johnson, T. G., Leandro, J., and Hartmann, T. (2020). Exploring the relation between flood risk management and flood resilience. Water Sec. 9, 100059. doi: 10.1016/j.wasec.2020.100059
Eakin, H. C., Parajuli, J., Hernández Aguilar, B., and Yogya, Y. (2022). Attending to the social–political dimensions of urban flooding in decision-support research: a synthesis of contemporary empirical cases. Wiley Interdiscip. Rev. Clim. Change 13, e743. doi: 10.1002/wcc.743
Epstein, S. (1994). Integration of the cognitive and the psychodynamic unconscious. Am. Psychol. 49, 709.
Feng, Y., and Nassauer, J. (2022). Community experiences of landscape-based stormwater management practices: a review. Ambio 51, 1–18. doi: 10.1007/s13280-022-01706-2
First Street Foundation (2022). First Street Aggregated Flood Risk Summary Statistics Version 2.0 (2.0) [Data set]. Geneva: Zenodo.
Flotemersch, J., and Aho, K. (2021). Factors influencing perceptions of aquatic ecosystems. Ambio 50, 425–435. doi: 10.1007/s13280-020-01358-0
Frantzeskaki, N. (2019). Seven lessons for planning nature-based solutions in cities. Environ. Sci. Policy 93, 101–111. doi: 10.1016/j.envsci.2018.12.033
Han, S., and Kuhlicke, C. (2019). Reducing hydro-meteorological risk by nature-based solutions: what do we know about people's perceptions? Water 11, 2599. doi: 10.3390/w11122599
Hobbie, S. E., and Grimm, N. B. (2020). Nature-based approaches to managing climate change impacts in cities. Philos. Trans. R. Soc. B 375, 20190124. doi: 10.1098/rstb.2019.0124
Jarvie, J., Arthur, S., and Beevers, L. (2017). Valuing multiple benefits, and the public perception of SUDS ponds. Water 9, 128. doi: 10.3390/w9020128
Jorgensen, A., Hitchmough, J., and Calvert, T. (2002). Woodland spaces and edges: their impact on perception of safety and preference. Landscape Urban Plann. 60, 135–150. doi: 10.1016/S0169-2046(02)00052-X
Kellens, W., Terpstra, T., and De Maeyer, P. (2013). Perception and communication of flood risks: a systematic review of empirical research. Risk Anal. Int. J. 33, 24–49. doi: 10.1111/j.1539-6924.2012.01844.x
Kellens, W., Zaalberg, R., Neutens, T., Vanneuville, W., and De Maeyer, P. (2011). An analysis of the public perception of flood risk on the Belgian coast. Risk Anal. Int. J. 31, 1055–1068. doi: 10.1111/j.1539-6924.2010.01571.x
Kline, R. B. (2015). Principles and practice of structural equation modeling. New York, NY: Guilford publications.
Kuang, D., and Liao, K.-H. (2020). Learning from floods: linking flood experience and flood resilience. J. Environ. Manag. 271, 111025. doi: 10.1016/j.jenvman.2020.111025
La Loggia, G., Puleo, V., and Freni, G. (2020). Floodability: a new paradigm for designing urban drainage and achieving sustainable urban growth. Water Resour. Manag. 34, 3411–3424. doi: 10.1007/s11269-020-02620-6
Lechowska, E. (2018). What determines flood risk perception? A review of factors of flood risk perception and relations between its basic elements. Nat. Hazards 94, 1341–1366. doi: 10.1007/s11069-018-3480-z
Lechowska, E. (2021). Approaches in research on flood risk perception and their importance in flood risk management: a review. Nat. Hazards 111, 1–36. doi: 10.21203/rs.3.rs-214525/v1
Lennon, M., Scott, M., and O'neill, E. (2014). Urban design and adapting to flood risk: the role of green infrastructure. J. Urban Des. 19, 745–758. doi: 10.1080/13574809.2014.944113
Li, J., and Nassauer, J. I. (2021). Technology in support of nature-based solutions requires understanding everyday experiences. Ecol. Soc. 26, 35. doi: 10.5751/ES-12838-260435
Liao, K.-H. (2012). A theory on urban resilience to floods: a basis for alternative planning practices. Ecol. Soc. 17, 15. doi: 10.5751/ES-05231-170448
Loewenstein, G. F., Weber, E. U., Hsee, C. K., and Welch, N. (2001). Risk as feelings. Psychol. Bull. 127, 267. doi: 10.1037/0033-2909.127.2.267
Lund, N. S. V., Borup, M., Madsen, H., Mark, O., Arnbjerg-Nielsen, K., and Mikkelsen, P. S. (2019). Integrated stormwater inflow control for sewers and green structures in urban landscapes. Nat. Sustain. 2, 1–8. doi: 10.1038/s41893-019-0392-1
Mariano, C., and Marino, M. (2018). Water landscapes: from risk management to a urban regeneration strategy. UPLanD J. Urban Plann. Landscape Environ. Des. 3, 55–74. doi: 10.6092/2531-9906/5846
Mcclymont, K., Morrison, D., Beevers, L., and Carmen, E. (2020). Flood resilience: a systematic review. J. Environ. Plann. Manag. 63, 1151–1176. doi: 10.1080/09640568.2019.1641474
Meerow, S., Helmrich, A. M., Andrade, R., and Larson, K. L. (2021). How do heat and flood risk drive residential green infrastructure implementation in Phoenix, Arizona?. Urban Ecosyst. 24, 989–1000. doi: 10.1007/s11252-020-01088-x
National Academies of Sciences Engineering and Medicine (2019). Framing the Challenge of Urban Flooding in the United States. Washington, DC: National Academies Press.
Netzel, L. M., Heldt, S., Engler, S., and Denecke, M. (2021). The importance of public risk perception for the effective management of pluvial floods in urban areas: a case study from Germany. J. Flood Risk Manag. 14, e12688. doi: 10.1111/jfr3.12688
O'donnell, E., Thorne, C., Ahilan, S., Arthur, S., Birkinshaw, S., Butler, D., et al. (2020). The blue-green path to urban flood resilience. Blue-Green Syst. 2, 28–45. doi: 10.2166/bgs.2019.199
O'donnell, E. C., and Thorne, C. R. (2020). Drivers of future urban flood risk. Philos. Trans. R. Soc. A 378, 20190216. doi: 10.1098/rsta.2019.0216
O'neill, E., Brereton, F., Shahumyan, H., and Clinch, J. P. (2016). The impact of perceived flood exposure on flood-risk perception: the role of distance. Risk Anal. 36, 2158–2186. doi: 10.1111/risa.12597
Palazzo, E. (2019). From water sensitive to floodable: defining adaptive urban design for water resilient cities. J. Urban Des. 24, 137–157. doi: 10.1080/13574809.2018.1511972
R Core Team (2020). R: A Language and Environment for Statistical Computing. Vienna: R Foundation for Statistical Computing.
Rigolon, A. (2016). A complex landscape of inequity in access to urban parks: a literature review. Landscape Urban Plann. 153, 160–169. doi: 10.1016/j.landurbplan.2016.05.017
Rogers, B., Bertram, N., Gersonius, B., Gunn, A., Löwe, R., Murphy, C., et al. (2020). An interdisciplinary and catchment approach to enhancing urban flood resilience: a Melbourne case. Philos. Trans. R. Soc. A 378, 20190201. doi: 10.1098/rsta.2019.0201
Sevenant, M., and Antrop, M. (2011). Landscape representation validity: a comparison between on-site observations and photographs with different angles of view. Landscape Res. 36, 363–385. doi: 10.1080/01426397.2011.564858
Sheppard, S. R. (2005). Landscape visualisation and climate change: the potential for influencing perceptions and behaviour. Environ. Sci. Policy 8, 637–654. doi: 10.1016/j.envsci.2005.08.002
Silva, M. M., and Costa, J. P. (2018). Urban floods and climate change adaptation: the potential of public space design when accommodating natural processes. Water 10, 180. doi: 10.3390/w10020180
Slovic, P., Finucane, M. L., Peters, E., and Macgregor, D. G. (2004). Risk as analysis and risk as feelings: some thoughts about affect, reason, risk, and rationality. Risk Anal. Int. J. 24, 311–322. doi: 10.1111/j.0272-4332.2004.00433.x
Slovic, P., Macgregor, D. G., and Peters, E. (1998). Imagery, Affect, and Decision Making. Eugene: University of Oregon.
Sutton, R. M., and Farrall, S. (2005). Gender, socially desirable responding and the fear of crime: are women really more anxious about crime?. Br. J. Criminol. 45, 212–224. doi: 10.1093/bjc/azh084
Tempels, B., and Hartmann, T. (2014). A co-evolving frontier between land and water: dilemmas of flexibility vs. robustness in flood risk management. Water Int. 39, 872–883. doi: 10.1080/02508060.2014.958797
U.S. Census Bureau. (2019). 2015–2019 American Community Survey 5-year Estimates. Available online at: https://www.census.gov/programs-surveys/acs/data.html
Wachinger, G., Renn, O., Begg, C., and Kuhlicke, C. (2013). The risk perception paradox: implications for governance and communication of natural hazards. Risk Anal. 33, 1049–1065. doi: 10.1111/j.1539-6924.2012.01942.x
Keywords: urban flooding, stormwater management, nature-based solution (NBS), flood risk perception, community resilience, landscape design, climate change adapataion
Citation: Li J, Nassauer JI, Webster NJ, Preston SD and Mason LR (2022) Experience of localized flooding predicts urban flood risk perception and perceived safety of nature-based solutions. Front. Water 4:1075790. doi: 10.3389/frwa.2022.1075790
Received: 20 October 2022; Accepted: 23 November 2022;
Published: 09 December 2022.
Edited by:
Silvia Di Francesco, University Niccolò Cusano, ItalyReviewed by:
Chiara Arrighi, University of Florence, ItalyAntonio Annis, University for Foreigners Perugia, Italy
Copyright © 2022 Li, Nassauer, Webster, Preston and Mason. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Jiayang Li, amlheWFuZ2xpJiN4MDAwNDA7dWZsLmVkdQ==