Figures
Abstract
Climate change increases water crises’ frequency and intensity, requiring more effective solutions and water management. Environmental scholars have found gender-diverse teams make more sustainable, efficient, and equitable solutions. However, women remain under-represented in water management, hindering effective decision-making. Further, water crisis communications carry inextricable mortality reminders: In a water crisis, access to a life-sustaining resource is threatened. Terror Management Theory stipulates that these mortality reminders activate predictable human responses to assuage the anxiety from thinking about our own demise, responses that include strengthening ingroup identities and distancing from outgroups. These responses may exacerbate gender biases already present in homogeneous management contexts, potentially limiting effective water management outcomes. We empirically tested effects of (a) a standard mortality reminder, (b) a water crisis reminder, and (c) a painful but non-life-threatening control reminder on judgements of same- or different-gender water managers. Ambivalent sexism (a framework consisting of hostile and benevolent sexism subcategories) was included as a moderator variable, revealing significant interacting effects based on participants’ benevolent sexism levels. Benevolent sexism (BS) stems from the belief that women need to be protected by men, creating prejudiced behaviours that may appear protective but in actuality harm gender equity. We found (a) water crisis reminders evoked responses similar to the standard mortality reminders and (b) significant interacting effects emerged regarding existential threat, benevolent sexism, and decision-makers’ gender. Specifically, control group males rated the water manager more positively, regardless of gender; male participants higher in BS rated the woman water manager more positively, regardless of reminder condition; and female participants lower in BS rated the woman water manager less positively in the threat reminder conditions. Reasons for these outcomes are explained alongside implications for effective water management. Thus, water crisis communications, mortality reminders, and sexism can influence gender bias in water management, negatively influencing sustainable water outcomes.
Citation: Smith LKM, Bergsieker HB, Wolfe SE (2025) Human dimensions in water crisis management: Gender bias in water manager appraisals and implications for water decision-making. PLOS Water 4(11): e0000460. https://doi.org/10.1371/journal.pwat.0000460
Editor: Guillaume Wright, PLOS: Public Library of Science, UNITED KINGDOM OF GREAT BRITAIN AND NORTHERN IRELAND
Received: February 3, 2025; Accepted: October 16, 2025; Published: November 19, 2025
Copyright: © 2025 Smith et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: Preregistration, research materials, and data are available online at https://osf.io/bp4fy/?view_only=3651d3701e8546de8455c288be194fd4 (anonymized for blind-peer review).
Funding: This work was supported by the Social Sciences and Humanities Research Council of Canada (Insight Grant 435-2018-0142 to SW; Vanier Canada Graduate Scholarship to LS). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.s.
Competing interests: The authors have declared that no competing interests exist.
1.0 Introduction
As water mismanagement intensifies the climate crisis, worsening flooding and drought risks and posing dire threats to people of all genders, water-related decision makers remain disproportionately men [1–5]. Water crises are complex and hard-to-predict, yet outcomes require deliberate, collaborative, interdisciplinary decision-making [6]. Despite male-dominance at the top of water decision-making hierarchies in both the Global North and South [1–4,7], the most effective solutions for complex climatic problems require decision-maker diversity [8–13]. Beyond water, gender and leadership scholars find persistent gender homogeneity in top management across sectors: men are typically the majority in top decision-making and management contexts [14,15]. Further, even when some women are present, gender and other intergroup biases (based on group identity) may prevent these minority members from being heard [16], considered valuable, or viewed as influential compared to dominant male counterparts [17,18]. This limits opportunities for more equitable [8], innovative [19,20], and effective environmental solutions [10–13,21]. Yet, the influence of gender bias in water management remains underexplored.
Complicating water decision-making dynamics further is the persistent, threatening climate and water messaging that can trigger psychological responses to assuage existential, mortality anxieties. Psychological responses to these threats, detailed in Section 1.2, include ingroup preference and outgroup othering that undermine diversity efforts [22–25]. Decades of social psychology research on Terror Management Theory (TMT) demonstrate that mortality threats can exacerbate intergroup biases [26–28]. Yet the influence of threatening water reminders remains underexplored in TMT and water communication research, despite water’s essential role in human survival, myriad water-related catastrophes connected to climate change, and the desperate need for decision-maker diversity in this space [29,30].
Bridging largely disparate fields – climate, existentialism, and social psychological sciences – we investigated how mortality reminders may impact intergroup gender biases related to appraisal of female versus male water managers. To examine how ingroup gender bias may present in water decision-making contexts, we tested the influence of a typical mortality reminder and a water crisis reminder on evaluations of female versus male water decision-makers. The typical mortality reminder used to evoke mortality salience (MS) in TMT studies involves two questions asking the participant to think about their own death (see Section 2.2.2). Our water crisis reminder involved the same questions but about drowning rather than death. Given the established male-dominance in top water decision-making and management roles [31], men’s appraisal of female decision-makers was our primary focus, with a larger sample size; exploratory analyses also tested women’s decision-maker appraisals. Our data extend research on human responses to existential threats (e.g., within TMT) and on how mortality reminders may contribute to gender bias and influence decision-making, heeding calls from climate scholars to pay critical attention to water crises and responses [32] and from leadership scholars to fill behavioral gaps in the literature [33].
First, we outline foundations of current water crisis research, required solutions, and water management practices as a rationale for our water focus. Second, we discuss gender, gender biases, and their role in decision-making, particularly within water management. Third, we briefly describe TMT’s principles, human response to existential threats, and related impacts on gender bias and group decision-making.
1.1 Climatic water crises management
Water availability and quality are central concerns for human life in a changing climate, both threatened by predicted extreme weather conditions [29,30]. Although technical solutions (e.g., water infrastructure, sanitation, desalination) have been previously prioritized [34,35], water scholars increasingly understand water crises as unique governance and management challenges, due to climatic and physical boundary uncertainties [36,37]. This shift in thinking has increased demand for collaborative, transdisciplinary, intersectional water management and solutions [38,39]. Scholars argue that diverse, collaborative groups are required for these water solutions [40–43]. Gender diverse decision-making groups make more pro-environmental and equitable decisions [9,44–46], which generate more innovative and creative water solutions [34,35,47]. Here, gender diverse groups mean those with similar numbers of women and men as research on alternate gender identity groupings is lacking. To address complex water crises, diverse input is required to identify, develop, and implement effective water solutions. When underrepresented groups are absent from these discussions, their insights are unheard and their needs often go unmet, exacerbating the harms they face [8,12,16,21].
Whereas much gender-water literature focuses on the Global South [48,49], our research focused on the Global North (or Western societies), recognizing that the power and resources here are needed for making positive changes to water management. Northern water decisions also affect the South, as water privatization companies based in the Global North increasingly expand into the South [50]. Lastly, the Global North offers clear opportunities to improve water-related decision-making. For example, over 100 Indigenous reserves remain under boil water advisories in Canada [48,49] and water contamination concerns persist in the U.S. (e.g., Flint, MI; [49]).
1.1.1 Workplace gender bias and diversity in water management.
Although the diversity required to obtain optimal water solutions could and should include various identity intersections (e.g., race, class, age), here we focused on gender.
We focused on gender as the powerful few in water decision-making are mostly men; women are largely absent in water management and leadership roles [3,4,51–53]. For example, in water utilities – responsible for safe drinking water and wastewater transportation and treatment – only 23% of managers are women [3]. The Global North treats water management as a highly technical field [34,54], with increasing reliance on technology for monitoring, control, and treatment, and this is not viewed as stereotypical women’s work [55,56].
In addition to gendered stereotypes around the type of work entailed in water management, persistent leadership stereotypes can be a barrier for women entering management roles [14,57,58]. Conventional leadership roles are often viewed as requiring stereotypically masculine, agentic traits of assertiveness, dominance, and competitiveness, which contradict entrenched societal expectations around female behaviors [59,60]. Women who act agenticly – often associated as good leadership behavior for men – are viewed more negatively and are rated as poor leaders, in part because women are expected societally to display more communal traits – being gentle, sensitive, and nuturing [61,62]. This negative appraisal is especially prominent in male-dominated fields, such as engineering [63], where water management often falls. However, business scholars argue that transformational leadership, which relies on collaborative, communal traits and interpersonal skills – qualities typically associated with and a style more often displayed in women [64] – is what leads to improved environmental outcomes from both employees and by the leaders’ organization overall [65–67].
Increasing groups’ gender diversity is not easy and, at times, can lead to unintended negative outcomes [68]. For example, analyses linking more women on corporate boards to increased board performance may overlook reverse causation if firms that are performing well have additional resources to hire and support women in higher roles [69]. In addition, a solo woman or marginalized group member hire is unlikely to feel valued or to impact group decisions, as they will often be viewed as an outgroup [70]. Such complexities do not negate goals to address representation or inclusion concerns, but should be acknolwedged to be an ‘honest knowledge broker’ who considers their role and that of science in evidence-based policy and decision-making [69,71].
Social psychology scholars have found abundant evidence of gender bias in workplaces, particularly for women in management or leadership [59]. This workplace bias stems in part from gender role incongruity [72], whereby women are presumed to take on stereotypically feminine roles – those that are caring, nurturing, or requiring communal skills – and face biases or criticism when they enact gender incongruent roles – those thought to require masculine traits, such as assertiveness and competition [14,73].
Although gender stereotypes regarding water work and leadership may explain some of women’s absence from these decision-making spaces, an inextricable aspect of human psychology remains. Within social psychology, TMT scholars have demonstrated how mortality reminders and awareness – also termed mortality salience – influence gender stereotypes and ingroup biases. Management and organizational behavior scholars have called for inclusion of TMT insights [74] and initial studies have findings applicable to workplace dynamics [75–77], discussed further below. In addition, the founding premise for the current work, water-specific TMT researchers have found that drowning reminders evoked MS similarly to traditionally used mortality reminders [78]. Our psychosocial defenses to these threats, explained below, may help explain lacking diversity – in both ideas and perspectives – in water management [79].
1.2 Terror management theory: Human response to existential threat
All humans know their lives will one day cease; the existential dread evoked by this awareness activates psychological defenses to push this anxiety aside [80–83]. However, these defenses can trigger unconscious biases against those seen as others – whether of different gender, race, or other social identity [26–28]. Over 30 years of social psychological research has aided in TMT development and validation [80,81,84]. A brief TMT overview is provided, detailing gender bias intersections, before we describe its potential applications in water crisis decision-making and our research.
TMT scholars have identified predictable human responses to mortality reminders that serve to temper the existential anxiety that these reminders induce [85,86]. Specifically, explicit, direct mortality reminders (e.g., thinking about one’s death, attending a funeral, experiencing another’s death) evoke proximal defenses; we deny our vulnerability or mortality, distract ourselves from the reminder, or rationalize that we are not at risk [86]. When mortality reminders are more subtle or indirect (e.g., the word ‘death’ flashed subliminally or a delay follows a proximal mortality reminder, allowing it to exit focal attention), distal defenses occur; people seek to boost their self-esteem by more vigorously supporting their worldviews and those who are aligned with their values, distancing from those who are different, and supporting ‘hero-projects’ that will outlast their own physical existence [86]. In sum, proximal defenses serve to minimize the mortality threat while distal defenses provide ways in which we may symbolically survive.
Distal defenses were our focus due to the ingroup preference and outgroup derogation – or intergroup biases – that can occur. Prior TMT scholars have found mortality reminders increase ingroup preference regarding political opinions [87,88], religion [83], race [89], nation [90,91], societal norms [82], and gender [92]. Recent TMT work has identified that climate change reminders can serve as mortality reminders, instigating similar anxiety defenses as traditional death-related stimuli [24,93–96]. Water crises were explicitly tested in prior research and found to activate death thoughts similarly to traditional mortality reminders [78]. Thus, when water, a life-sustaining resource, is threatened, subtle mortality reminders may activate these intergroup biases to bolster self-esteem and ensure ingroup survival.
Prior TMT-gender research is presented briefly below to illustrate potential gender biases that can occur from such reminders.
1.2.1 Terror management theory and gender.
Gender identity is a component of self-identity and self-esteem [97,98]; following distal mortality reminders, one may seek to strengthen positive connections with gender identity to protect their self-esteem, potentially resulting in ingroup gender bias [99,100]. In male-dominated groups, mortality awareness can activate ingroup preferences, leading men to prefer other men and to dislike women, as observed by Hoyt et al. [76] and Arndt et al. [99], resulting in gender discrimination. Due to preexisting gender and societal stereotypes (e.g., role congruity theory [72]), this reaction can increase gender equity challenges in homogeneously gendered spaces.
This MS-related gender bias repeats in leadership appraisals where gender stereotype threats may occur. Women are often viewed negatively when they occupy roles traditionally seen as masculine or participate in men-dominant groups [14,60,72,99]. Business-focused TMT researchers explored the impact of MS on stereotype and ingroup-gender bias effects [100]. These scholars found that when mortality was salient (vs. not), women preferred the woman candidate, and men preferred the man candidate – a clear indication of ingroup biases. In Hoyt et al.’s [76] second study, the more stereotypically agentic candidate was preferred regardless of gender when mortality was salient – though men preferred only agentic-men candidates, not agentic-women candidates [100]. Further, MS can increase use of agentic leadership traits when participants define an effective leader [77]. MS has also been shown to increase preference for charismatic leaders and decrease preference for relationship-oriented leaders [101]. These altered preferences may increase bias against those who do not display these attributes (e.g., women) in existentially threatening scenarios. This bias is particularly troubling when we consider that transformational leaders are those needed for improved environmental outcomes [102]. If agentic traits are preferred following mortality reminders, people may be predisposed to leaders who may ‘look the part’ but may not necessarily be best suited to providing effective, equitable climate solutions [8,9,45].
1.3 Mortality, gender bias, and water decision-making
Given the potential for water crises to activate mortality anxieties and reinforce stereotypical gender biases in leadership roles, hindering decision-maker diversity and optimal water outcomes, in this study we examined how mortality reminders influence perceptions of women versus men in decision-making. After establishing that our specific life-threatening water reminder about drowning effectively evoked MS relative to a control prompt in an earlier study [78], here we compared the influence of a typical mortality reminder and this life-threatening water reminder of drowning (relative to a control message) on appraisal of a fictional “water manager” woman versus a fictional “water manager” man, among a sample of educated (e.g., with post-secondary education) adult men. The education constraint was important to correlate with approximate education level of water managers. Men were chosen as our focal group due to their hierarchical dominance in water-related decision-making and positions of power, as described above. We made no hypotheses for the women participants in this investigation, so our corresponding women sample was treated as exploratory. We hypothesized that if typical or drowning-related MS increased ingroup gender bias, men exposed to MS would rate a decision-making man more positively than a decision-making woman, than in a control condition (described below). Decision-makers in this study were not explicitly described as leaders, so we did not expect stereotype threat effects from gender role incongruity to outweigh ingroup bias effects (preferring one’s own gender). We included a measure of ambivalent sexism [103] to capture further insights on individual differences in sexist attitudes that might predict potential gender biases. We expected that participants in typical MS or drowning MS interventions would score higher on this sexism measure than those in the control condition due to activated ingroup gender biases.
2.0 Materials and methods
2.1 Ethics statement
The research was approved by the Office of Research Ethics at the University of Waterloo (ORE #42726) and participants provided informed, written consent to participation online and re-consented to their data usage after learning the full study purpose.
2.2 Participants
We recruited 656 adult participants from the United States and Canada (161 women, 495 men; aged 18–75) from September 5–November 2, 2022, via Prolific, an online crowd-sourcing platform, to complete an approximately 20-minute survey for about $3.25 CAD. The sample size, with its implied stopping rule, was determined to balance desired power (.95 to detect medium effect size of d = .25 at.05 alpha error probability) and resource availability (e.g., financial constraints within the research budget). Men were the focal group, so were recruited at a 3:1 ratio to women. Enrollment was limited to participants with (a) a minimum bachelor-level education to approximate experience to those in water management roles and (b) Prolific approval ratings over 90% to ensure quality responses as recommended for online research [104].
Prolific automatically screened out responses when attention checks failed, surveys timed out, or there was evidence of non-human activity, removing 8 women and 33 men. Our exclusion criteria (e.g., incomplete intervention prompts, responses >3 SDs from mean) did not identify any additional removals, yielding final samples of 153 women and 453 men.
2.3 Procedure and design
We employed a randomized between-subjects 3 (Intervention: typical MS vs. drowning MS vs. control) x 2 (Vignette decision-maker gender: woman vs. man) preregistered study design, displayed graphically in Fig A in S1 Text, with a delay between the mortality-related and gender manipulations. Our pre-registration is available at https://osf.io/x2vab/?view_only=4bd8a4c757bb4f5f85cd7105a5235829.
2.3.1 Cover survey and delay tasks.
Participants were first presented a cover survey to mask study purpose and avoid inadvertently priming all participants with mortality [105]. This survey is commonly used to bolster the cover story in TMT research [105,81]. As per standard TMT research procedures [94,106,105], to extend the delay period and allow MS to activate distal defenses, participants completed three delay tasks: The Positive and Negative Affect Schedule (PANAS; [107]), Rosenberg Self-Esteem Measure [108], and State-Trait Anxiety Inventory [109]. Prior TMT researchers have found that longer delays (e.g., > 5 minutes) strengthen defense effects [110].
2.3.2 Independent variables.
Participants were then randomly assigned to one of three intervention groups (Supplementary Materials 2: Control, Typical MS, Drowning MS) and asked two, open-ended questions regarding physical and emotional experiences of an event, modeled after the Mortality Attitudes Personality Survey (MAPS; [82]). The control event was an anxiety-inducing but non-life-threatening painful dental visit, used as the control in roughly two-thirds of TMT studies [81,105], the typical MS group described their own death, while the water-specific MS group described drowning, a scenario that successfully evoked MS in a prior study [78].
Following the delay, participants were randomly assigned to read one of two vignettes (Text A in S1 Text) describing a water-related decision made by either ‘Jennifer’ or ‘John’, cuing the respective decision-maker identities of woman versus man. This naming difference elicited significant gender biases in appraisals a candidate described as a woman versus man in past research where ‘Jennifer’ was deemed less competent and offered a lower salary in a hypothetical hiring scenario compared to identically qualified ‘John’ [111]. Similarly, our vignettes were identical in all ways other than name and pronouns used throughout the text.
We investigated appraisals of others based on their presumed gender as evidenced via names and pronouns in the vignette. Given the psychosocial factors involved in judgements about others, where people are often viewed as the gender they present or perform [112], we addressed gender (as an expression of identity; [98,113]) rather than sex (based on one’s physical body or genitalia). We also included self-disclosure for transgendered, non-binary, and gender-non-conforming identities, but few participants (<1%) disclosed these identities.
2.3.3 Dependent variables.
After reading the vignette, participants rated their positive or negative perceptions of the decision-maker on both “Likeability” (16 items) and “Competence” (12 items). These measures, adapted from social psychology and leadership studies [27,101,114], included items such as “I agree that the decision-maker is friendly”, “I would enjoy working with the featured decision-maker”, and “I trust the decision-maker” rated on Likert scales. Factor and correlational analyses indicated that these measures were highly related in both samples (rmale = .67 & rfemale = .73, ps < .001), with almost identical patterns of results. As such, we deviated from pre-registration for parsimony by combining the scales into one “Positivity” measure with excellent reliability in both samples (Cronbach’s αmale = .93; αfemale = .96). Beforehand, we rescaled the 5-point “Competency” scale to an 8-point range (like “Likeability”) so the two measures had matched minima and maxima, suitable for averaging together (see Text B in S1 Text).
2.3.3 Moderating and demographic variables.
Ambivalent sexism was measured via the Ambivalent Sexism Inventory (ASI [103]; Text C in S1 Text), which includes 22 items rated on a Likert scale from 0 to 5. This well-validated and widely used sexism measure (see [115] for a comprehensive review) assesses both hostile and benevolent sexism (HS and BS). HS originates from patriarchal society ideals, leading women to be viewed as inferior, and BS from female reproductive roles, leading to preference for traditional values and roles for women [103,116]. For example, in a Turkish sample, high HS individuals view women managers less positively than men [117]. The ASI has been used in prior TMT studies [118,119]. We also collected participants’ demographic information (e.g., age, gender, location, education).
3.0 Results
As described in preregistration, after data cleaning (e.g., removal of outliers and/or erroneous responses), general linear models (GLMs) with orthogonal planned contrasts were used to test differences across conditions (e.g., interventions) for all dependent variables. Contrasts and reasons for their use are summarized in Table B in S1 Text.
Data were analyzed via linear regression with the GLM procedure in SPSS 28. We used pre-registered orthogonal contrasts to test hypothesized effects of interventions, decision-maker gender, and their interactions (see Table B in S1 Text for contrast details). When intervention effects were tested for influence on appraisal of specific decision-maker gender, focal gender was dummy coded as the reference group and follow-up models explored effects for the non-focal gender (Table 2, simple effects). Exact p values were reported, and effect size expressed as η2p. Table 2 displays unstandardized regression estimates (b) and SE. Unless specifically indicated, age and education did not significantly moderate appraisal scores.
3.1 Descriptive Statistics
Participant distributions into experimental conditions and means are shown in Table 1. Most participants had a master’s degree or higher (90% of male sample, 95% of female sample) and their ages ranged from 20 to 71 years (Mmale = 40; Mfemale = 41).
Bivariate correlations for dependent variables are displayed in Table C in S1 Text. Planned analyses of the male sample then exploratory analysis of the female sample are reported below.
3.2 Condition effects among male participants
Positivity scores are shown by intervention condition and decision-maker gender in Fig B in S1 Text.
Planned contrast GLMs tested condition differences. A significant effect of the Threat versus Control contrast emerged for positivity (b = -.10, SE = .05, t(1, 447) = -2.07, p = .039, η2p = .009), indicating that after a mortality or drowning threat, decision-makers (regardless of gender) were rated significantly less positively (by 0.29 points, 95% CI: -0.56, -0.02) than the control.
Analysis of ASI as a dependent variable revealed no effects so we deviated from preregistration to analyze each ASI subscale as a predictor, consistent with their conceptualization and operation primarily as stable individual difference variables [103,115]. Thus, HS (M = 1.82, SD = 1.19) and BS (M = 2.14, SD = 0.98) were mean-centred and added as moderators in separate models. The HS moderation model showed no evidence of interaction effects. BS significantly interacted with DM Gender (b = .15, SE = .07, t(1, 447) = 2.27, p = .024, η2p = .012, see Fig 1) and the Threat versus Control contrast (b = -.10, SE = .05, t(1, 447) = -2.08, p = .039, η2p = .010, see Fig 2).
Women (but not men) decision-makers were rated more positively by those with higher benevolent sexism scores. Dashed lines indicate 95% confidence bands.
Dashed lines indicate confidence bands (95%).
We probed these interactions among men higher versus lower in BS (±1 SD from the mean [120]; see Table 2). Men higher in BS showed significant simple effects of decision-maker gender (b = .25, SE = .09, t(1, 447) = 2.81, p = .005, η2p = .018) – rating women (vs. men) decision-makers more positively (.50 points higher, 95% CI: 0.15, 0.85) – and of the Threat versus Control contrast (b = -.20, SE = .07, t(1, 447) = -3.05, p = .002, η2p = .021) – rating decision-makers more negatively (by.61 points, 95% CI: -1.00, -0.22) after MS. No significant effects emerged among lower-BS men (all ts < 1; see Table 2).
3.3 Condition effects among female participants
For female participants, initial planned contrast results showed significant effects of decision-maker gender for positivity (b = .24, SE = .11, t(1, 147) = 2.10, p = .037, η2p = .029).
We again explored mean-centred HS (M = 1.07, SD = 1.00) and BS (M = 1.62, SD = 0.93) as potential moderators. For positivity ratings, a significant three-way interaction (see Table 2) indicated that BS moderated the Threat x DM Gender interaction (b = .21, SE = .08, t(1, 147), = 2.48, p = .014, η2p = .042). As such, higher and lower BS were probed. Among higher-BS women, only one marginally significant (simple) effect emerged (see Table 2): Women (vs. men) decision-makers were rated marginally higher (by 0.54 points, b = .27, SE = .15, t(1, 147) = 1.79, p = .075, η2p = .022).
Among lower-BS women, however, a significant Threat x DM Gender simple interaction (b = -.23, SE = .11, t(1, 147) = -2.16, p = .033, η2p = .032) indicated that MS effect on positivity varied based on decision-maker gender (see Fig 3), so we decision-maker gender was dummy-coded to test MS simple effects specific to men or women decision-makers among lower-BS women. MS did not affect ratings of men decision-makers (b = 0.19, SE = 0.15, t(1, 147) = 1.25, p = .215, η2p = .011). Conversely, for ratings of women decision-makers, a marginally significant simple effect for the Threat versus Control contrast emerged among lower-BS women (b = -.28, SE = 0.16, t(1, 147) = -1.80, p = .075, η2p = .022), such that women decision-makers were rated 0.84 points more negatively (95% CI: -1.76 – 0.08) after MS reminders than control instructions.
Dashed lines indicate confidence bands (95%).
4.0 Discussion
Overall findings are explained below, organized by sample, first discussing general positivity results before considering BS influence on positivity ratings and susceptibility to threat conditions. We then connect findings to theoretical and practical implications for diversity efforts within water crisis management.
4.1 Male participants: overall decision-maker appraisal and benevolent sexism
Contrary to our prediction that appraisal of women decision-makers would be more negative in threat conditions, we found no such interactions among male participants. Instead, significant overall MS effects on positivity emerged, discussed below.
4.1.1 Threat effects on decision-maker appraisal.
Following typical and drowning MS, decision-makers regardless of gender were rated marginally less positively by male participants. Plausibly, participants may have seen these decision-makers as outgroups, thus rating decision-makers more negatively (than in the control) to create psychological distance from a threatening other to offset mortality anxieties. Although participants had similar (or higher) education levels to water managers and decision-makers, we did not specifically recruit participants working in water sectors (or ask participants to imagine themselves as working in this sector). If participants were instead limited to water managers or had been led to consider the decision-makers as part of their ingroup (as in, with some shared interest), perhaps decision-makers would have been rated more favorably after mortality reminders, as observed in other TMT [121,122] and intergroup bias research [123,124].
4.1.2 Benevolent-sexism-specific findings among male participants.
Our investigations of variation in participants’ BS yielded several moderation findings. First, among higher-BS men—but not lower-BS men—appraisal positivity differed for the man versus woman decision-maker. Specifically, we found that higher-BS men rated the woman decision-maker more positively, regardless of condition (e.g., control, mortality, drowning). As seen in Fig 1, ratings of only ‘Jennifer’ (not ‘John’) as a decision-maker increased with higher BS.
A possible explanation for this result comes from gender-social psychology literature. These scholars have identified that women are often rated more favorably than men in general, a concept referred to as the “women-are-wonderful” (WAW) effect [125,126]. This effect aligns with the content of BS, which involves an expectation that women are kind, gentle, and agreeable [126]. Plausibly, this WAW effect may have outweighed any underlying intervention differences, suggesting opportunities for subsequent research. With a larger sample size or alternate wording, intervention differences might be more evident. Further, highly favorable ratings of women among men higher in BS may not persist when women occupy gender-incongruent roles, such as management or leadership, where such communal traits are not stereotypically valued. For instance, if the decision-maker had been explicitly described as a leader or in a top managerial position, outcomes may have been more negative for women decision-makers due to gender role incongruity [72]. Importantly, BS correlates with positive attitudes towards women [103]. This correlation does not mean BS is harmless: It represents beliefs that women should remain in stereotypically traditional care-taking and domestic roles, with men maintaining dominion over women [103]. In addition, management scholars have found that BS can prevent women from being assigned challenging but important skill-development tasks, reducing opportunity for promotion and leadership [127]. Further, social psychologists have found that while higher BS predicts stronger support for workplace equity policies, support persists only for policies that funnels women into stereotypically feminine positions [128]. Thus, depending on how men viewed women – whether they believed women belong in traditional, nurturing roles – influenced their appraisal of the woman water decision-maker. Again, it must be emphasized that positive appraisal does not translate to equitable treatment at work if women are well-liked but not respected and rewarded for their achievements [129,130].
Our second BS-specific finding among male participants was that BS significantly moderated overall effects of the threat conditions (e.g., mortality, drowning) versus control condition on positivity ratings. Higher-BS participants may have sought to distance themselves from the decision-maker, regardless of decision-maker gender, working in a role related to an existential threat as a strategy to avoid mortality anxieties. Thus, rating the decision-maker more negatively allowed them to deny mortality risk and keep death anxiety at bay. Similar to the results observed for decision-maker gender, effects of threat condition emerged only among male participants higher (but not lower) in BS.
4.2 Female participants: overall decision-maker appraisal and benevolent sexism
Analyses of our smaller female sample were exploratory, so we did not hypothesize expected appraisal outcomes, yet compelling findings emerged and are discussed below.
4.2.1 Benevolent-sexism-specific findings among female participants.
Considering BS, a significant Threat x DM Gender x BS interaction transpired. Intriguingly, lower-BS women showed effects that were originally predicted to occur among men. Lower-BS women rated women, but not men, decision-makers marginally less positively in threat conditions (typical mortality or drowning) than the control. That this effect would emerge specifically among women lower (not higher) in BS may initially seem puzzling, given that lower-BS women may be less gender congruent themselves (reducing likely backlash against other women in gender-incongruent roles). Indeed, in prior research, women’s BS was related to disapproval of agentic women [131]. However, lower-BS women have been found to hold women in leading roles (a group historically facing barriers) to higher, more exacting standards [132]. In our vignette, the woman decision-maker chose financial savings over improved environmental outcomes, potentially contradicting expectations held by lower-BS peers for women in leadership to uphold higher standards for moral behavior [132]. This contradiction may have evoked harsher appraisals.
4.3 Water-specific mortality threat influence on decision-maker appraisal
A central goal of our research was to determine whether water-specific MS effects on decision-maker appraisal resembled those of typical MS – that is, we wanted to determine whether water threats would influence our participants’ appraisals of decision-makers in similar ways to a typical mortality threat. Although we observed aforementioned threat effects relative to the control condition (see 4.1.1), drowning MS did not emerge as more or less potent than typical MS. This aligns with prior empirical exploration of MS in water crisis communication [78,133] and TMT-Climate research more broadly (see: [94]). As such, water crisis communicators – whether communicating water crises to the general public or within water policy – should consider implications of both generic and water-specific threatening language in decision-making as this can influence how decision-makers may be viewed and, thus, what actions may or may not result. In scenarios where gender role incongruency may evoke gender stereotypes, such as when increasing involvement of underrepresented leaders or managers in water management, problem framing and language choice warrants consideration lest MS further exacerbate existing gender biases.
4.4 Implications for terror management theory and gender
Our findings contribute to TMT, gender role theory, and their intersection. Some but not all findings supported prior TMT and gender studies research. We found MS effects to be moderated by BS for (a) higher-BS men’s appraisal of decision-makers and (b) lower-BS women’s appraisal of female decision-makers. Potential explanations for convergence and divergence are provided below, considering timing and recent TMT critiques, before discussing connections to leadership and management literatures. Water management specific implications are discussed in Section 4.5.
First, MS may have been influenced by study recruitment timing (2021–2022), amid an ongoing pandemic, recognized as a society-wide mortality reminder [134,135]. Elevated ambient MS could have diminished comparisons between threat and non-threat (control) conditions. A non-pandemic study might detect stronger MS effects, perhaps even outweighing the WAW effects observed here to trigger stronger intergroup biases, as found in prior TMT research [23,28,91,136–138].
Importantly, the relatively modest MS effects (η2p < .01 among male participants; reversed and non-significant among female participants) in our high-powered study can contribute additional evidence to current debates surrounding TMT. Recent meta-analyses [139,140] of large-scale MS replication experiments have added key null effects to TMT literature and revised the average TMT effect size estimate downward to r = 0.18 [141]; our pre-registered experiment stands to strengthen the scientific record by clarifying when and for whom (in our study, based on BS levels) predictions derived from TMT may or may not replicate.
Further research into gender-specific appraisal differences following mortality threats would provide necessary insights into gender biases exacerbated by MS and thus influencing climate and water decision-making. For example, Florian et al. [142] found that MS caused gender-congruent girls and boys to prefer interacting with other gender-congruent peers more than those who were gender incongruent, while those who were gender incongruent preferred gender-incongruent others. Due to various stereotypes and norms regarding women in decision-making roles, such as incongruent gender roles and human responses to existential threats that can magnify these stereotypes, our findings indicate that judgements made about decision-makers under threat lead to complex psychosocial reactions. This has significant, meaningful implications for water management, water policy, and gender equity efforts. By examining implicit sexism factors, particularly BS, we can detect patterns relevant to real-world decision-making and management scenarios. Improved understanding of TMT and gender role implications within realistic-but-threatening decision-making scenarios may help clarify how to best increase diversity in these spaces.
4.5 Implications for water crisis practitioners
Our findings and literature review suggest an arduous path to increasing diversity and equity in water management for more sustainable outcomes. We first present leadership applications (as significant power lies in these positions), followed by workplace connections, and then suggest options for tackling gender biases in these contexts.
We respond to calls for increased behavioral research within leadership theory [33]. We argue that greater gender diversity – and specific attention to benevolent presentations of ambivalent sexism – is needed in high-ranking positions to obtain more effective, durable, and widely applicable solutions to impending water crises. With diverse leaders, more versatile, innovative, and effective water solutions can serve the needs of many [143,144].
To achieve gender inclusion, workplace culture must also be transformed to support women, particularly in spaces like water management that have been frequently dominated by men [145]. Despite increased education and recruitment rates for women in traditionally male-dominated fields, women’s attrition rates persist, and women less often progress to management and leadership positions [57,146]. Several organizational and cultural factors contribute to these attrition rates. Workplaces often lack sufficient childcare accommodations (while women remain predominant caregivers in households [147,148]) and organizations with few women in leadership roles lack non-male role models and have limited training, mentorship, and sponsorship opportunities for women [57,146,149]. In addition to remedying these issues, our findings suggest that strategies that address BS in the workplace would be beneficial given the effects we found for both higher-BS men and lower-BS women. BS, as a component of ambivalent sexism, is less obvious than HS because the latter more often manifests in overtly misogynistic acts or statements that individuals can readily perceive, address, or avoid [115,150]. Counter to our initial predictions, we did not find that men rated women (vs. men) water managers more negatively in the threat conditions specifically; however, the observed tendency for men with higher BS scores to evaluate water managers differently merely based on their name (Jennifer or John) points to the persistence of gender bias. Again, that higher-BS men in this instance evaluated women more positively than men does not ensure equitable workplace treatment. For example, social psychological research indicates that in male-dominated occupations, female leaders are penalized more harshly than their male counterparts for mistaken decisions [151]. As such, incorporating BS-aware equity strategies may help to foster gender diversity among management and leadership, particularly in fields like water crisis management where bias-exacerbating mortality threats are common.
Lastly, while our participants held similar education levels to water managers, testing these patterns among actual decision-makers and leaders would provide valuable insights for enhanced water solutions. Still, our findings indicate that gender biases and implicit, ambivalent sexism modify appraisal of same- and different-gender decision-makers. Fortunately, strategies exist to limit harmful biases and increase cooperation among diverse decision-making groups. For example, increased intergroup contact – more interaction with individuals from different groups – decrease prejudice and outgroup derogation [124,152]. Identifying similarities among group members also reduced bias in studies by psychologists [153] and TMT scholars specifically [27]. Recent research on allyship has shown that proactive allyship (e.g., demonstrating inclusion before biased behaviors occur, such as including underrepresented groups on projects they might not be otherwise), even more than reactive allyship (responding to biased behavior after or as it happens), effectively reduces discrimination felt by underrepresented employees [145]. Water managers should incorporate such strategies when seeking to increase diversity among decision-makers. These changes may be difficult and complex, but the benefits to sustainable, equitable water outcomes are worthwhile and urgently needed [40–43].
5.0 Conclusion
Climate change will increase water crises – in turn, increasing mortality awareness – and require effective, pro-environmental, impactful solutions that provide water security for all. Environmental scholars have shown diverse decision-making groups are well-equipped for these solutions, so water management must make equity and diversity in decision-making a priority. Our research responds to calls to fill water gaps in climate change recommendations [32] and behavioral gaps in leadership studies [33]. We have shown how life-threatening topics can impact decision-maker appraisals through activated mortality anxieties, which in turn can determine whose voices are heard, whose ideas are valued, and, ultimately, what solutions are implemented. Group dynamics are complex; our results show gender dynamics, particularly BS, within typically men-dominant settings only add to this complexity. Given the potential – if not likelihood – for gender and intergroup biases to influence decisions in water crisis management, increased mortality saliency with more potent climate change consequences, and the perhaps impossibility of removing mortality reminders, diversity efforts in these workplaces must be intentional and strategic. For instance, diversity strategies that emphasize differences can fail to engage or motivate those with (and without) power [154]. Rather, efforts that stress similarity, collective goals, proactive allyship, and interaction with different others have been effective for improving inclusion. Empirically supported strategies to minimize intergroup biases should coincide with attention to retaining underrepresented groups. Though our initial research focused on gender in water management, other identity intersections are necessary to consider within water decision-making and are worth incorporating in future research [155]. To ensure such diversity is obtainable and equitable, intergroup biases that occur at individual and structural levels within water management – and other homogeneous spaces – must be addressed. A broader, nuanced understanding of water crises – and potential solutions – is possible with greater diversity at decision-making tables.
Supporting information
S1 Text. Supporting information list of legend.
Fig A. Visual representation of study procedure. Table A. Prompt and condition-specific phrasing. Text A. Water decision-making vignette. Text B. Decision-maker positivity measure. Text C. Ambivalent Sexism Inventory (Glick et al., 1996). Table B. Planned contrasts and explanations. Table C. Bivariate correlations by sample. Fig B. Mean positivity ratings by condition among male participants.
https://doi.org/10.1371/journal.pwat.0000460.s001
(DOCX)
Acknowledgments
The authors would like to thank the funders of this research, the participants, and reviewers for their insight and feedback regarding this work.
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