ORIGINAL RESEARCH article
Visual Exposure to Natural Environments Decreases Delay Discounting of Improved Air Quality
- 1Human Behavioral Pharmacology and Decision-Making Laboratory, Department of Health Education and Behavior, University of Florida, Gainesville, FL, United States
- 2Department of Psychology, University of Florida, Gainesville, FL, United States
- 3Department of Psychology, University of Montana, Missoula, MT, United States
Poor air quality contributes to nearly 7 million premature deaths annually and remains a major public health concern. In order to directly address the future of air quality and current emissions, some economists and policy makers have stressed adopting a “zero discount rate” (or lowest possible) to promote clean air quality now and in the future. A low discount rate is also associated with individual health behaviors (e.g., exercise and lower rate of substance abuse). But what influences the psychology of decision-making that is relevant to the discount rate of air quality and public health outcomes, and individual health? The present experiments evaluated differences in such decision-making (i.e., delay-discounting) in the context of improved air quality with visual exposure to natural vs. built environments. Results showed that individuals exposed to natural scenes discounted improved air quality less (i.e., made more future-oriented decisions, Experiment 1), and this may be related to expanded space perception (Experiment 2). These results are the first to suggest that delay discounting of air quality (or any environmental outcome), similar to money, is malleable, and can be influenced by exposure to natural relative to built environments. These findings have implications for influencing long-term, individual health, and environmentally relevant decision-making and improving individual and public health related outcomes such as air quality.
The World Health Organization (WHO) estimates that poor air quality resulting from emissions (e.g., from automobiles/industries/factories) contributes to nearly 7 million premature deaths worldwide each year (1). Further, the American Lung Association (ALA) estimates that over 50% of Americans breathe poor quality air that could lead to health problems. Improving air quality could drastically reduce the burden of stroke, heart disease, and lung cancer, as well as acute and chronic respiratory diseases, namely asthma (1). Air pollution is also a significant contributor to local and global biodiversity loss (2), and can interact with other anthropogenic influences such as climate change to impact the distribution of plant species, food availability, and reproductive success of wildlife species in polluted areas. Importantly, air quality does not constitute a single problem, but represents an array of threats to humans, public health, plants, and animals (1, 2).
In order to directly address the future of air quality and current emissions, some economists and policy makers have stressed adopting a “zero discount rate” (or the lowest possible) to promote clean air quality now and in the future [see Weitzman et al. (3) for discussion]. Delay discounting, or the discount rate, can be described as the degree to which outcomes in the future are devalued (4, 5). A zero discount rate implies that the future cannot be discounted relative to the present. In other words, to conserve clean air quality in the future citizens and policy makers must act in ways that drastically reduce negative anthropogenic influences on air quality immediately (e.g., substantially reduce emissions now from industry/factory/private car use), and thereby discount the future of air quality less. Behavior of society and individuals, however, shows that we discount the future at an alarmingly steep rate.
Why do we discount the future when steep discounting can be harmful for our health and the environment? In the case of both the environment and personal health, negative consequences may be relatively far in the future and probabilistic (e.g., climate change and lung cancer). When future consequences fail to influence present behavior, people act in ways that emphasize present bias (6). For example, it is convenient to drive a private car immediately despite increased emissions, rather than plan to take public transportation associated with an increased delay, but decreased overall emissions—a decrease that might improve air quality in the region they live in. Additionally, if many other people are also driving a private car, there may be less incentive to decrease one's own private car use. That is, individual emissions may seem minimally impactful compared to larger group emissions. Although many factors are at play in this example (e.g., immediate vs. delayed consequences, self vs. public health, and probability of experiencing an outcome), the basic tension of choice surrounding smaller sooner vs. larger later environmental outcomes is clear.
Although evidence suggests delay discounting is in part a function of individual differences [genetic influences (7); neurocognitive influences (8)] a distinct line of research has emerged focusing on the malleability of individual discount rates in laboratory settings—and subsequent changes in real world decision-making. This may represent implications for global reductions in delay discounting [e.g., drug use, overeating (9–13)]. Specifically, experimental manipulations have been designed to reduce or preclude the effects of delay on the value of money in order to facilitate a decrease in delay discounting. For example, Daniel et al. (10) showed that future episodic thought resulted in decreased delay discounting of money, and also less ad libitum energy consumption in obese individuals [see also (9); as well as (13) for examples of decreased delay discounting in monetary choices that correlated with decreased drug use].
This line of research would suggest that such methodologies used to decrease delay discounting of monetary outcomes [e.g., working memory training (14); visual exposure to nature (15–17); future episodic thought (13, 18); framing effects (19–21); for a review see Koffarnus et al. (22)], might also be used to decrease delay discounting of environmental outcomes more generally, and air quality specifically. This would lend theoretical evidence to targeting the same underlying cognitive and decision-making processes to enable decreased delay discounting of air quality (i.e., greater valuation of air quality in the future). We also targeted a potentially practical method to inform intervention to reduce delay discounting of air quality (e.g., increased exposure to natural spaces in cities or schools, incorporation of visual scenes of nature inside buildings).
Delay discounting of environmental outcomes and related measures is a burgeoning area of research (6, 23–26). A central discussion point is the degree that delay discounting processes operate in a similar fashion for far-reaching collective environmental decisions as they do for personal monetary decisions. Most research in the area is on personal monetary decisions. There are reasons to expect both fundamental differences [e.g., environmental decisions can be driven more by emotion than monetary decisions (27)] and fundamental similarities [e.g., strong positive correlations between money and environmental commodity discount rates (28)] between monetary and environmental decision-making processes. Such a discussion has theoretical and practical implications for the generality of delay discounting, associated factors influencing decision-making processes, and real world health and environmentally relevant behaviors [see Arbuthnot et al. (29) for discussion of the relation between delay of gratification and sustainability; see Hirsh et al. (30) for discussion of delay discounting as a psychological construct of sustainable behavior].
Other than a single study examining standard magnitude effects (31), no research to date has fused these specific areas of research to examine the malleability of discount rates in the context of environmental outcomes generally, or air quality specifically (i.e., at present comparisons are based solely on correlational measures). As such, it is currently unknown if the same manipulations designed to minimize effects of delay on monetary value would also minimize the effects of delay on air quality value (or the value of any environmental outcome). If delay discounting of air quality is malleable, this would offer vast implications for the ability of society to structure the environment to promote decreased delay discounting of air quality—and healthier long-term decision-making (i.e., a lower discount rate).
In the present experiments, we examined whether visual exposure to natural as opposed to built environments would result in decreased delay discounting of improved air quality (Experiment 1). We also examined potential underlying mechanisms driving this effect (Experiment 2), as has previously been shown with monetary outcomes (15–17). If delay discounting of improved air quality is decreased with visual exposure to natural as opposed to built environments, this would suggest (1) that how individuals value the future of air quality is malleable; (2) delay discounting of air quality can be reduced in a way that also reduces delay discounting of money, suggesting fundamentally similar, rather than fundamentally different underlying decision-making processes; and (3) the effects of decreasing delay discounting (i.e., increasing future valuation, increasing self-control) through visual exposure to natural environments is not domain specific (i.e., does not just apply to money), and may represent a generalizable and broad beneficial influence of exposure to natural environments on decision-making. We hypothesized that visual exposure to natural as opposed to built environments would decrease delay discounting of improved air quality.
Experiment 1 Materials and Methods
Sixty-six undergraduate students were recruited from an introductory psychology course and received course credit for participation. This study was carried out in accordance with the recommendations of University of Montana Institutional Review Board (IRB). The protocol was approved by the UM IRB. All subjects gave written informed consent in accordance with the Declaration of Helsinki.
Setting and Apparatus
Participants were tested individually in a quiet experimental room containing a desk, chair, computer, and mouse. The room was well lit with overhead florescent lighting. Participants were not permitted to have personal belongings or cell phones on their person while participating in this experiment. Experimental manipulations and data recording were programmed using E-Prime 2.0®, and survey and demographic data were collected using Qualtrics® (Provo, Utah). The monitor used was ~33 cm high, and 58 cm wide.
The stimuli used in the present study have been used previously in delay discounting research, as well as attention restoration research [e.g., (15, 16, 32)]. Participants in the natural condition viewed photographs of nature (e.g., lakes, forests, and mountains), and participants in the built condition viewed photographs of built environments (e.g., cities, buildings, and roads). Each condition specific photograph contained primarily visual scenes from either natural or built scenes. In other words, nature scenes did not contain built aspects within the photograph and vice versa. The brightness of the photos were approximately equal across both natural and built photographs. For examples of the stimuli used, please see Berto (32) and Berry et al. (15).
Participants first read and signed informed consent. Participants were then seated in front of the computer and instructed to choose whichever option they preferred in the task, and that there were no “right” or “wrong” answers [similar to instructions provided by Odum et al. (33)]. Similar instructions were also provided on the screen, and led participants through the task. Participants used the mouse to progress through the experiment. Participants were assigned via block randomization to either the natural or built condition. Before the start of the delay discounting task (described below) and between each delay block, participants viewed either natural or built photographs. Photographs were displayed for 10-s each. Prior to the delay discounting task participants viewed 25 photographs, and between each delay block viewed five photographs (which were randomly selected from the original set of 25). With the exception of the differing photographs across natural or built conditions, all experimental procedures were identical.
In the delay-discounting task, participants made choices between experiencing hypothetical air quality improvements immediately or in the future. During the choice portion of the overall procedure, there was no limit on how much time the participants could take to select their choice in the delay discounting task. Participants read a hypothetical scenario that stated that the local county government was considering changes to its emissions policies (e.g., reducing pollutants of nearby factories) to test the effects of air quality on human health and local wildlife. These changes would result in a reduction of particulate output and pollutants in their area as measured by the Air Quality Index (particulate matter, carbon monoxide, sulfur dioxide, nitrogen dioxide, and ground level ozone; 0 = very good air quality to 500 = hazardous air quality) designated by the United States Environmental Protection Agency. As a result, substantial improvements in air quality would be experienced. The local government was considering making these changes for a number of days, after which time the air quality index would return to its former level, and the government was considering making these changes either immediately or sometime in the future. The Air Quality Index was selected as a means to describe air quality improvements to facilitate understanding of the hypothetical scenario for several reasons. First, it is an actual measure used by the U.S. Environmental Protection Agency. Second, it offers an accessible description of air quality, and finally many people in the U.S. are familiar with this measure. This hypothetical scenario was similar to the scenario presented by Hardisty and Weber (28).
For each trial in the adjusting amount delay discounting procedure employed in the present study, participants chose between an immediate smaller option, or a delayed larger option. Each choice screen read, “Would you rather experience [Y days of improved air quality] immediately,” or “Y days of improved air quality in [delay]?,” starting with values of 50 days immediately or 100 days after a delay on the first trial at each delay. Participants selected either the immediate (fewer days of improved air quality) or delayed outcome (more days of improved air quality) to progress, and the choices switched sides throughout the experiment. The mouse pointer was programmed to center after each selection. The immediate amount increased or decreased based on the participant's response as previously described [see Du et al. (34); Rodzon et al. (35) for a detailed descriptions of the titration procedure], so that the point at which the smaller sooner amount was equivalent to the larger later amount (i.e., the indifference point) was determined by the end of 10 trials at each delay. Delays tested were 1 day, 1 week, 1 month, 6 months, 1 year, 5 years, and 25 years in that order. Following all experimental procedures, basic demographic information was collected (e.g., age and sex).
To evaluate decision-making within the delay discounting task, two measures were assessed: Area Under the Curve (AUC) and k values. Area under the curve (AUC) was used to evaluate smaller sooner vs. larger later decision-making in the delay discounting air quality task, and as a comparison between decision-making across conditions. To calculate AUC the delays and indifference points at each delay (i.e., the point at which the smaller sooner and larger later amount was equivalent) were first normalized. Then the area underneath the discounting curve was calculated using the equation:
where x2 and x1 represent successive delays and y1 and y2 represent the indifference points associated with those delays (36). These values were then summed, resulting in AUC calculations that range from 0 to 1, with lower numbers representing preference for smaller immediate outcomes (i.e., higher discount rates), and higher numbers representing preference for larger delayed outcomes (i.e., lower discount rates). A two-tailed Mann Whitney U-test was then used to test for potential differences in AUC across natural and built conditions. Values for AUC were not normally distributed, so statistical analyses presented do not assume Gaussian distributions (i.e., a Mann Whitney U-test was used). The second measure of discounting, k values (which represent degree or “rate” of discounting), were examined using the widely employed simple hyperbola (4):
where V is the subjective value of the reward, D is the delay to receipt of the reward, and k is the degree to which the value of the reward decreases with delay. The values of A and D are predetermined based on the value used within the research context [e.g., if the delayed reward used is 100 dollars (or days of improved air quality), then the numerator is 100]. k values are then compared across conditions (using a Mann Whitney U-test to account for non-normal distributions).
Experiment 1 Results
Of the 66 participants, 57% were female. The mean age was 23.62 years (SD = 7.79). Chi square (sex, race) and a t-test (age) comparing demographics across natural and built conditions indicated no significant differences across groups for these variables (sex, p = 0.451; race, p = 1.00; age, p = 0.633).
Figure 1 displays the AUC for the natural and built conditions. Participants who viewed scenes of natural as opposed to built environments chose to experience more days of improved air quality with a delay, to fewer days of improved air quality immediately (i.e., higher AUC values; Natural Condition Mean = 0.514, SE = 0.054; Built Condition Mean = 0.357, SE = 0.055). A two-tailed test confirmed these visual assessments showing significant differences in AUC across natural and built conditions (Mann-Whitney U-test; U = 383.5, p = 0.041). Similar results were revealed when testing k parameter values across natural and built conditions (Mann-Whitney U-test; U = 335, p = 0.041).
Figure 1. The top panel displays mean AUC for the natural (filled bar) and built (open bar) conditions. Vertical lines represent the standard error of the mean. Asterisks represent statistically significant differences in AUC between the natural and built conditions. The bottom panel displays median indifference points across natural (filled circle) and built (open square) conditions as a function of delay. Delays spaced equidistantly to facilitate inspection of all values (with x-axis labels showing specific delays assessed).
Experiment 1 Discussion
Experiment 1 findings showed that those who viewed photos of nature discounted air quality less than those who viewed photos of built environments, suggesting that delay discounting of air quality is malleable. It is untested, however, if similar mechanisms underlie these behavioral effects as has been shown with monetary outcomes. Specifically, time and space perception appear to be related to reduced delay discounting of monetary outcomes with visual exposure to nature. To determine if these mechanisms also underlie decisions related to improved air quality with visual exposure to natural vs. built environments, we also examined time and space perception, as time/space perception has been predicted to influence both delay discounting and differentially affected by viewing natural vs. built environments (16, 37). We predicted that both time and space perception would be expanded with visual exposure to natural as opposed to built environments.
Experiment 2 Materials and Methods
Forty-two undergraduate students were recruited from an introductory psychology course and received course credit for participation. This study was carried out in accordance with the recommendations of University of Montana Institutional Review Board (IRB). The protocol was approved by the UM IRB. All subjects gave written informed consent in accordance with the Declaration of Helsinki. The setting and apparatus, stimuli, procedure and data analysis for the discounting data were identical to the methods used in Experiment 1.
Following the completion of the discounting portion of the study, participants then answered several questions to assess time and space perception. Specifically, “How many minutes would you estimate have elapsed since signing the informed consent?,” and “Picture yourself immersed in the images you saw on the screen throughout the study. On a scale of 1 (constricted)−10 (expanded), how does the space feel around you when you do this?” Finally, basic demographic information was collected.
Experiment 2 Results
Of the 42 participants, 71% were female. The mean age was 20.48 years (SD = 3.46). Chi square (sex, race) and a t-test (age) comparing demographics across natural and built conditions indicated no significant differences across groups for these variables (sex, p = 0.303; race, p = 0.687; age, p = 0.347).
Figure 2 displays the AUC for the natural and built conditions for Experiment 2. Participants who viewed scenes of natural as opposed to built environments chose to experience more days of improved air quality with a delay, to fewer days of improved air quality immediately (i.e., higher AUC values; Natural Condition Mean = 0.548, SE = 0.071; Built Condition Mean = 0.376, SE = 0.073), although these differences only trended toward standard levels of significance (Mann-Whitney U-test; U = 151.5, p = 0.103). Similar results were observed when testing k parameter values across natural and built conditions (Mann-Whitney U-test; U = 113.5, p = 0.065). Despite the lack of significant differences observed across the natural and built conditions, the effect was in the predicted direction, similar to the outcomes observed in Experiment 1.
Figure 2. The top panel displays mean AUC for the natural (filled bar) and built (open bar) conditions. Vertical lines represent the standard error of the mean. The bottom panel displays median indifference points across natural (filled circle) and built (open square) conditions as a function of delay. Delays spaced equidistantly to facilitate inspection of all values (with x-axis labels showing specific delays assessed).
Participants estimated a similar passage of time in minutes in both the natural and built conditions [Natural Condition Mean = 20.0, SE = 1.8; Built Condition Mean = 21.1, SE = 1.5, unpaired t-test, t(40) = 0.47, p = 0.64]. Participants in the natural condition, however, reported significantly expanded space perception relative to those in the built condition [Natural Condition Mean = 5.6, SE = 0.50; Built Condition Mean, M = 3.8, SE = 0.59; t(40) = 2.26, p = 0.03].
Experiment 2 Discussion
Experiment 2 results showed a trend toward reduced delay discounting of air quality outcomes with viewing natural as opposed to built environments. This trend however, was not statistically significant. There is also some indication that space perception is expanded with exposure to natural as opposed to built environments, but less so for time, partially replicating previous results (37).
First and foremost, these results offer the first direct evidence that viewing nature scenes can cause people to be future-oriented in their approach to air quality decisions: When people viewed nature scenes, they were more likely to trade bad days now for a better future. This finding has multiple novel implications: (1) Delay discounting of air quality is malleable acutely in an experimental context, (2) processes underlying delay discounting in environmental vs. monetary outcomes may be similar, and (3) although more research is needed, there are potential broad benefits of exposure to natural environments for human decision-making that emphasizes future rather than present outcomes, (4) expanded space perception may contribute to these outcomes, however results in this domain remain preliminary. We discuss each of these in turn.
Delay Discounting of Air Quality Is Malleable
Those who viewed photographs of natural as opposed to built scenes chose to experience more days of improved air quality in the future, to fewer days of improved air quality immediately. These results are the first to show that delay discounting in the context of environmental outcomes generally, and air quality more specifically, is responsive to acute experimental manipulations of natural or built photograph exposure. In particular, environments in which we spend our time appear to influence how individuals value future air quality. Some economists have stressed adopting the lowest possible discount rate associated with environmental outcomes to promote a healthier future (i.e., cleaner air). More access and increased exposure to natural/green spaces may facilitate individuals and society to place greater value on future rather than present air quality (thereby decreasing discount rates), and potentially other environmental outcomes.
Some mechanisms Underlying Delay Discounting of Environmental and Monetary Outcomes May Be Similar
Although little direct data exist, there has nonetheless been some discussion concerning exactly how similar the decision-making processes surrounding monetary and environmental discounting are to each other. For example, Gattig and Hendrickx (27) have suggested that decisions of risk and time related to the environment are driven more by emotion than decisions regarding money. Hardisty and Weber (28), however, have proposed that decisions for environmental and monetary outcomes are driven by similar underlying processes, as evidenced by the positive correlations between delay discounting of environmental and monetary commodities. Although necessary to establish similarities in decision-making processes [see Green and Myerson (38) for discussion of similarities and differences between delay and probability discounting], no previous experiments have tested whether the same manipulations designed to minimize the effect of delay in the context of monetary outcomes, might also minimize the effects of delay in the context of air quality outcomes (or other environmental outcomes). These results are the first to provide experimental evidence to the discussion—showing that decreased delay discounting of improved air quality also results from visual exposure to natural as opposed to built environments, as has been shown with delay discounting of money (15–17). These data lend support to the hypotheses that decision-making processes underlying environmental and monetary outcomes may be more similar than different. More research is needed to better understand similarities and differences between monetary and environmental decision-making.
What might account for the similarities? The expansion of time and space perception have been isolated as a potential mechanisms driving decreases in delay discounting with visual exposure to natural environments (16, 37), as time and space perception and temporal attention and delay discounting are related [e.g., (21, 37, 39)]. Expansion of space perception but not time perception with exposure to natural environments was demonstrated in Experiment 2 of the present study, lending partial evidence to these mechanisms. Berry, Repke, and other colleagues have speculated that expansion of time and/or space perception induced by visual exposure to natural environments may facilitate bridging the gap between current choices and future consequences. In addition to differences in time perception, previous research has shown differences in mood (40, 41), as well as differences in attention (32) and eye movements [e.g., saccades and fixations (42)] that are associated with tracking scenes of natural vs. built environments, each of which also influence delay discounting [e.g., attention (43); mood (44)]. All of these factors might apply equally across all domains that involve some form of delay discounting, including monetary and air quality decisions. More research is needed to squarely identify the mechanistic drivers of decreased delay discounting with exposure to natural as opposed to built environments [for other examples of differences in cognition and behavior with exposure to natural environments see Rutiku et al. (45) for differences in electro encephalography responses and cortical alpha activity with visual exposure to task irrelevant natural or built environments; as well as (46) for increases in creative problem solving with immersion in natural environments].
Practical Implications of Exposure to Nature on Air Quality
Although more research is needed to understand the mechanistic underpinnings, these findings have initial implications for how society might consider structuring environments to promote sustainable decision-making geared toward clean air in the future. Future research might identify if, for example, cities might be structured with more natural and green spaces to promote long term, future oriented decision-making that could subsequently benefit the environment (e.g., walking or taking public transportation rather than driving a private car). Increased implementation of natural spaces within cities, workplaces, and schools, as well as natural scenes within buildings could increase happiness and well-being (40), and also outcomes related to short-term impulsive decision-making [e.g., (15, 16)], and long-term environmental health (the present study).
This research combined with previous studies suggests that beyond frequent findings of increased happiness [e.g., (40)], improved attention [e.g., (32)], and reduced stress [e.g., (41)], exposure to natural as opposed to built environments also influences decision-making in the context of delay discounting, an important predictor of real world behavior [see also (47); for an example of increased cooperation with exposure to nature]. Reductions in delay discounting of air quality in real world situations will be necessary to address the effects of current and future emissions for our health and the health of our ecosystems (48). Importantly, exposure to natural as opposed to built environments may facilitate a beneficial and reciprocal interaction between humans and our ecosystems, with focus toward maximizing future ecosystem health, and therefore human health. Although delay discounting as a process (specifically a low discounting rate) has been considered as a potential fundamental aspect needed to engage in long term sustainable behaviors (30), more research is needed to understand the association between rate of delay discounting and environmentally relevant behaviors.
Several limitations exist. Our air quality scenarios are necessarily hypothetical. Research has shown, however, that decisions about hypothetical outcomes in a laboratory context are associated with real world behavior and choices involving delays (49, 50). By using a hypothetical scenario, however, we are able to show that air quality preferences are systematically influenced by delay, and the present procedure may represent the best way to study these relations under controlled conditions. Further, actual decision-making should be tested in future studies to more broadly address the influence of nature exposure on the value of air quality. Willingness to pay questions or scenarios in which individuals pay for improved air quality would offer increased breadth to the present findings. An additional limitation was the homogenous undergraduate student sample. This sample limits the generality of the findings. Future studies should examine these questions in older adult populations, as older adults tend to be involved in decision-making processes more than young people. Simultaneously, given improved air quality may be less likely to occur in the lifetime of an older adult, this may lead to higher discount rates. It is also unknown how an individual's experience with fluctuating air quality might contribute to the present findings.
It is also unknown how long such effects last, or exactly the “dose” of nature that is required to induce such effects. It should also be noted that the content of the photos used, such as lakes and forests, may not be representative of many natural environments and spaces. The same is true for the built environment photographs used in the present study. A large proportion of humans spend time in a combination of natural and built environments, and the current photos captured only one environment or the other. Additional studies parametrically incorporating both natural and built content within the photographs will help increase generalizability of these findings. Although the purpose of the present study was to compare the effects of natural vs. built environments on discounting of improved air quality, it should be noted that no neutral condition was used for further comparison. However, previous research (15) has found a neutral geometric condition to yield no differences in degree of money delay discounting when compared to the built condition. Future research should determine if visual exposure to natural, built, or neutral photographs yield differences in discounting of improved air quality.
Additionally, although the present studies offer some clues as to mechanistic underpinnings of the observed effects, future fully-powered studies should examine underlying mechanisms, as research in this area remains extremely limited. Lastly, it is unlikely that an individual's behavior would be influenced by exposure to natural environments if there is little to no attention paid to such surroundings (i.e., benefits are unlikely to be gleaned from surrounding nature if an individual is engrossed in their iPhone). Despite these limitations, these data are the first to reveal promising outcomes in the context of human decision-making with exposure to natural environments that might ultimately inform conservation of our present and future local and global air quality and improvement in public health.
Data Availability Statement
All datasets generated for this study are included in the manuscript/supplementary files.
This study was carried out in accordance with the recommendations of University of Montana Institutional Review Board (IRB). The protocol was approved by the UM IRB. All subjects gave written informed consent in accordance with the Declaration of Helsinki.
MB contributed to the conceptualization, data collection, formal analysis, methodology and writing the original draft, and review and editing of the manuscript. MR contributed to the conceptualization, data collection and analysis, and review and editing of the manuscript draft. LC contributed space and materials and review and editing of the manuscript draft.
MB was funded in part by the National Institute on Drug Abuse Grant T32DA007209, and was also funded in part by the National Science Foundation under Grant EPS-1101342. Any opinions, findings, and conclusions or recommendations expressed in this material are those of the authors and do not necessarily reflect the views of the National Science Foundation.
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.
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Keywords: delay discounting, intertemporal choice, natural vs. built environments, air quality, sustainability, behavioral economics, conservation psychology
Citation: Berry MS, Repke MA and Conway LG III (2019) Visual Exposure to Natural Environments Decreases Delay Discounting of Improved Air Quality. Front. Public Health 7:308. doi: 10.3389/fpubh.2019.00308
Received: 28 April 2019; Accepted: 08 October 2019;
Published: 25 October 2019.
Edited by:Taiki Takahashi, Hokkaido University, Japan
Reviewed by:Sulaiman Mouselli, Arab International University, Syria
Giorgio Guariso, Politecnico di Milano, Italy
Copyright © 2019 Berry, Repke and Conway. 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: Meredith S. Berry, firstname.lastname@example.org