Abstract
Background:
Plant-based diets can have co-benefits for human and planetary health. Associations between environmental, climate and health concerns and dietary intake in US adults are understudied, particularly for underserved populations.
Objectives:
The study objectives were to assess how dietary choices motivated by the environment, climate and health vary by sociodemographic characteristics and how they relate to diet quality and intake frequency of different food groups in US adults with lower incomes.
Design:
The study design is cross-sectional.
Participants/Setting:
A web-based survey was fielded in December 2022 to 1798 US adults with lower incomes (<250% Federal Poverty Guidelines, FPG).
Main outcome measures:
Environmental, climate and health-related dietary motivations and diet quality and dietary food group intake frequency were assessed.
Statistical analyses:
Differences in mean dietary outcomes and dietary motivation ratings by sociodemographic characteristics were evaluated using ANOVA and Kruskall-Wallis tests. Associations between dietary motivations and diet quality scores and dietary intake frequency were examined using generalized linear models adjusted for sociodemographic covariates.
Results:
Younger adults, women and non-binary persons, racially and ethnically minoritized groups, and adults experiencing food insecurity reported higher environmental and climate dietary motivations; older adults, higher-income and food-secure adults reported higher health motivations. Agreeing with environmental (β: 2.28, CI: 1.09–3.47), climate (β: 2.15, CI: 0.90–3.40), and health-related (β: 5.27, CI: 3.98–6.56) dietary motivations were associated with higher diet quality scores, compared to those with neutral rankings. Similarly, agreement with environmental, climate, and health-related dietary motivations was associated with higher intake frequency of fish, fruits and vegetables, and plant proteins, but not with red and processed meat intake frequency. Of several climate mitigation behaviors presented, participants perceived meat reduction as least effective (p<0.001).
Conclusions:
Environment, climate, and health were positive motivators of several healthy dietary choices in US adults with lower incomes. Such motivators did not translate to lower intake frequency of red and processed meat.
Keywords: Climate change, dietary motivations, dietary intake, red meat intake, climate resilience, climate disparities
Introduction
Global climate change, driven by anthropogenic greenhouse gas emissions (GHGE) is one of the largest and most pervasive threats to human health and well-being today.1 On average, environmental impacts and GHGE are lower for foods derived from plants than for meat and animal products, particularly beef.2–5 In addition to promoting planetary health, increasing plant intake and reducing red and processed meat intake may lower risks of cardiovascular disease, type 2 diabetes, and some cancers.2, 6
The Dietary Guidelines for Americans recommend higher intake of vegetables, fruits, and lean proteins, and “lower consumption of red and processed meats” for a healthy dietary pattern.7 More than half of Americans report being willing to reduce red meat consumption,8 yet red and processed meat intake in the United States (US) persists at a high levels.9, 10 US consumer shifts to vegetable equivalents of animal products can greatly reduce food-related GHGE,3 but even single-item substitutions for beef can markedly lower individual carbon footprints while maintaining dietary quality.11 Thus, it is beneficial and feasible to move towards more sustainable and healthy plant-forward diets low in red and processed meats (plant-based diets) in the US. However, to achieve this goal and to ensure that future dietary recommendations are equitable and accessible, it is important to understand what motivates such behaviors in different populations.
Climate change can affect food access and quality, and may disproportionately affect historically marginalized populations, creating greater inequities in health outcomes and access to healthy foods.12, 13 The flexibility to shift to plant-based diets in the US may be a future advantage if climate change stresses food systems13 and meat costs rise.14, 15 Populations subject to social stressors may face unique barriers to adaptability to healthy plant-based diets, thus affecting climate resiliency.1, 16 Furthermore groups that have been historically marginalized are reportedly more likely to recognize societal issues as environmental problems,17 and to value purchasing sustainable food,18 yet valuation might not always translate into consumption of these foods due to access constraints or cost.8 Additionally, due to increasing prevalence of processed and marketed plant-rich foods, low-meat diets may not always translate to healthy plant-based diets,19, 20 an issue potentially magnified by limited access to fresh foods. These combined issues highlight the importance of understanding how environmental and climate motivations are associated with diet quality and protein intake in populations that have been socially and economically marginalized.
Attitudes towards meat intake and sustainable diets have been recently reviewed, and both the environment and health have been reported as motivators of meat-reduction behaviors; however, environmental impacts of meat reduction are often under-estimated, and the association between health motivations and meat consumption is inconsistent.21–24 The inconsistent associations between health motivation and meat consumption may result from the breadth of health concerns and nutritional knowledge in the US. Few studies have evaluated how environmental and health motivators are associated with dietary intake. In a previous observational study, lower red meat intake was associated with sustainability and climate motivations in university students, despite moderate ranking of the mitigating impact of dietary meat reduction on climate change.25 However, health-related motivations did not result in a reduction in red meat intake frequency among university students.25 In another observational study, climate change concern was associated with less frequent red meat intake in a large population-based sample of Italian adults, but not chicken and processed meat.26 Online experimental studies have shown that both environmental and health messaging are motivators for red meat reduction intent in convenience samples of US adults.27, 28 Yet, to our knowledge, the associations between environmental, climate, and health-related dietary motivations and overall dietary quality and frequency of intake of multiple specific protein sources has not been previously evaluated in the US, particularly in populations with lower incomes.
More research is needed to understand how environmental and health concerns and motivations are associated with diet quality and consumption of various proteins in different sociodemographic groups – and structurally-disadvantaged populations in particular.13 To address these research gaps, this study aims to evaluate how environmental, climate, and health-related dietary motivations in a sample of US adults with lower incomes relate to overall dietary quality and intake frequency of different food groups, and how these associations vary with sociodemographic characteristics. It was hypothesized that environmental, climate and health-related dietary motivations will be associated with lower red and processed meat intake frequency and higher diet quality scores.
Methods
Study Population
In December 2022, a web-based survey (Qualtrics) was fielded to US adults ages 18 and over with annual household income levels of less than 250% of the 2022 Federal Poverty Guidelines (FPG).29 Previously described,30 the survey assessed dietary intake frequency, environmental, climate and health attitudes, and sociodemographic variables. Recruitment of participants was facilitated by Prime Panels, an online survey recruitment platform designed for academic research that gathers quality samples representative of the US population and reaching underrepresented groups.31 The stated purpose of the study was “… to understand factors that affect your diet and health.” Data collection was ongoing from December 9 through December 22, 2022 with a goal of obtaining a sample size which exceeded minimum sample size requirements for an α=0.05, 80% power, and similar effect sizes from prior studies.25 A total of 2898 participants were invited to complete the survey. Participants who did not consent (n=227), failed to answer attention checks correctly (n=231), did not live in the US (n=89), did not meet the income criteria (n=531), or had non-differentiation in responses for multiple sections (n=22) were omitted. Data were further screened for participants who completed answers at an average rate of one second or less per question31 and no additional participants were removed, resulting in a final study population of 1798 participants. Participants were compensated with preestablished rates by the Prime Panels research panel through which they were recruited. Participant consent was obtained electronically. The study was determined to be exempt by the University of Michigan Institutional Review Boards.
Diet Quality and Food Group Intake Frequency
Food group intake frequency and diet quality were measured using the 30-day Prime Diet Quality Score (PDQS-30), a previously-validated screener designed to evaluate overall dietary quality by ranking diet according to consumption of healthy and unhealthy food groups.32, 33 Briefly, participants were asked about intake frequency of different food groups over the past month. Response options included seven categories: once a month or less, 2–3 times per month, 1–2 times per week, 3–4 times per week, 5–6 times per week, once a day, or 2 or more times per day. Each food group was categorized as healthy or unhealthy. The 14 food groups categorized as healthy included: dark green leafy vegetables; cruciferous vegetables; deep orange vegetables and tubers; other vegetables; citrus fruits; deep orange fruits; other fruits; beans, peas, and soy products; nuts and seeds; poultry; fish (not including shellfish); low fat dairy; whole grains; and liquid oils. The 7 food groups categorized as unhealthy included: white roots and tubers; red meat; processed meat (sum of processed red meats and other processed meats); refined grains and baked potatoes; sugar-sweetened beverages; sweets and ice cream; and fried foods eaten away from home. For each participant, healthy food category responses were assigned a value ranging from 0 (once a month or less) to 6 (2 or more times per day). Unhealthy foods were reverse coded. Thus, possible individual PDQS-30 scores ranged from 0 to 126 with higher scores indicating healthier diets.
To evaluate intake frequency of specific food groups, questions on frequency of intake were converted to times per day. For categorical frequency ranges, the midpoint was used and divided by 7 or 30 to convert weekly or monthly frequency to daily frequency. For processed meats, questions asked about both processed red meats and processed poultry but did not include processed fish. Red and processed meat intake frequency was calculated by summing daily intake frequency of red meat, processed red meat, and processed poultry. Fruit and vegetable intake frequency was calculated by summing daily intake frequency of all fruits and vegetables scored in the PDQS-30 score. Plant protein intake frequency included combining daily intake frequency of nuts and seeds with intake frequency of beans, peas, and soy products.
Environment, Climate, and Health Attitudes
Motivations for food and beverage choices.
Questions were asked about the extent to which food and beverage choices were motivated by concern for (1) the environment, (2) climate change, and (3) health. These questions have been used in prior research25 and asked “How much do you agree with these statements? I try to make food and beverage choices that…”: “Are good for the environment,” “Reduce my impact on climate change,” and “Are good for my health,” with a 7-point response scale ranging from 1= “Strongly Disagree” to 7= “Strongly Agree” for each item. Responses were classified as disagree (response of 1–3), neutral (response of 4, reference group) or agree (response of 5–7).
Perceptions of climate-friendly behaviors.
Items assessing perceived effectiveness of behaviors for combatting climate change have been previously described,25 and were modified from a scale developed by de Boer and colleagues.34 The questionnaire asked, “For each of the lifestyle changes, indicate whether you think this is an effective way of combatting climate change” (in random order): “Eat local, seasonal foods”, “Eat less meat”, “Drive less”, “Eat organic foods”, “Use less plastic”, “Save energy at home”, “Recycle.” Response options ranged from 1=“Not effective at all,” to 4=“Highly effective,” and included “Don’t know.” Responses of “Don’t know” (ranging from n=90 to n=226 per response) were excluded from statistical analyses.
Sociodemographic Variables
Sociodemographic data collected included self-reported age, gender, race and ethnicity, education, annual household income, and state of residence. For analysis, those self-identifying as female and transgender woman were classified as woman, male and transgender man were classified as man, and those responding as neither male nor female or “none of these” were classified as gender non-conforming. Due to small numbers in some response categories, race and ethnicity were reclassified as non-Hispanic Black, Hispanic, non-Hispanic White (includes Middle Eastern/North African as currently defined by US Census35), and a fourth group encompassing participants self-identifying as Asian, Native Hawaiian or Other Pacific Islander, American Indian or Alaska Native, or Multiracial/Multiethnic. Food security status was assessed using the US Household Food Security Survey Module and scores were categorized according to USDA guidelines.36 Food insecurity refers to individuals in the low or very low food security groups.
Statistical Analysis
First, descriptive statistics were used to examine participants’ sociodemographic characteristics. Then, means and standard deviations (SD) were calculated for PDQS-30 scores, red and processed meat daily intake frequency, and environmental, climate and health motivations by participants’ sociodemographic characteristics. Differences in means by sociodemographic characteristics were compared using one-way analysis of variance for PDQS-30 scores and motivations, and Kruskall-Wallis nonparametric tests for differences in means for red and processed meat intake frequency (due to the skewed distribution of red and processed meat intake frequency). Associations between environmental, climate and health motivations and dietary intake frequencies were examined using generalized linear models with a log link (to allow for interpretation of coefficients as percent difference), and gamma distribution (to account for the skewed distribution of dietary intake frequency). Frequency ratios (FR) were calculated by exponentiating the model coefficients; [FR-1] *100 represents percent higher frequency of consumption for each point on the perception scales. A generalized linear model with an identity link and normal distribution was used to evaluate associations between motivations and PDQS-30 scores, due to the normal distribution of the PDQS-30 scores. Models were adjusted for age, gender, race and ethnicity, education, %FPG, education, and environmental or health motivations, due to the potential influence of these variables on both dietary outcomes and environmental or health motivations.18, 25, 37, 38 Interactions between sociodemographic variables and red/processed meat intake frequency were examined for the outcome of PDQS-30. Wilcoxon signed-rank nonparametric tests were used to evaluate within-individual differences in mean ranking of the effectiveness of climate mitigation behaviors. Statistical significance was considered at p < 0.05. Statistical analyses were performed using SAS version 9.4.39
Results
Mean PDQS-30 score and red and processed meat intake frequency (times/day) are shown in Table 1. Mean diet quality score for this population (50.2) was less than half of the maximum score (126). Mean diet quality scores differed significantly by age (p=0.01), race and ethnicity (p<.001), education (p<.0001), %FPG (p=0.03), food security (p=0.004) and geographic region (p=0.03). Means were lowest for adults age 40–49, people self-identifying as non-Hispanic White, and groups with lowest education levels, lowest income, and food insecurity. Participants living in the Midwestern or Southern US had lower PDQS-30 scores than those living in the Northeastern or Western US. Mean intake frequencies of red and processed meat also differed by age (p<.0001), race and ethnicity (p=0.01), education (p=0.001), food security (p=0.04), and geographic region (p<.001). Red and processed meat intake frequency (times/day) was generally highest for younger age groups, with highest mean intake frequency observed for ages 30–39. People who identified as Hispanic had highest mean red and processed meat intake frequency, followed by those identifying as non-Hispanic Black, non-Hispanic White, and those falling into the racial and ethnic group including people identifying as Asian, Native Hawaiian or Other Pacific Islander, American Indian or Alaska Native, or Multiracial/Multiethnic. Red and processed meat intake frequency was highest for those with the lowest education level and those with food insecurity. Those living in the Southern and Midwestern US had the highest red and processed meat intake frequency, while those living in the Northeastern and Western US had the lowest intake frequency.
Table 1.
Sociodemographic distribution and mean with standard deviation (SD) diet quality score and dietary intake frequency for US adults with lower incomes (n= 1798) surveyed in December 2022.
| Sociodemographic Variable | n (%) | PDQS-30a | Red & Processed Meat Intake Frequency (times/day) |
||||
|---|---|---|---|---|---|---|---|
|
| |||||||
| Mean | SD | p-valueb | Mean | SD | p-valuec | ||
| All participants | 1798 (100) | 50.2 | 11.3 | 0.77 | 0.74 | ||
| Age (years) | |||||||
| 18–29 | 328 (18.4) | 50.2 | 11.3 | 0.01 | 0.89 | 0.79 | <0.0001 |
| 30–39 | 358 (19.9) | 49.5 | 11.5 | 0.91 | 0.85 | ||
| 40–49 | 330 (18.4) | 49.3 | 11.4 | 0.86 | 0.86 | ||
| 50–59 | 307 (17.1) | 49.5 | 11.4 | 0.67 | 0.63 | ||
| ≥60 | 475 (26.4) | 51.7 | 10.9 | 0.58 | 0.53 | ||
| Gender | |||||||
| Woman | 924 (51.4) | 50.4 | 11.6 | 0.44 | 0.73 | 0.70 | 0.12 |
| Man | 858 (47.7) | 49.9 | 11.0 | 0.81 | 0.79 | ||
| Gender non-conforming | 16 (0.89) | 52.9 | 9.4 | 0.63 | 0.61 | ||
| Race and Ethnicity | |||||||
| Non-Hispanic Black | 279 (15.5) | 52.4 | 11.4 | <0.001 | 0.81 | 0.82 | 0.01 |
| Hispanic | 171 (9.5) | 51.7 | 11.7 | 0.89 | 0.91 | ||
| Non-Hispanic Whited | 1237 (68.8) | 49.4 | 11.2 | 0.75 | 0.69 | ||
| A/NHPI/AIAN/M/Oe | 111 (6.2) | 50.8 | 10.6 | 0.63 | 0.76 | ||
| Education | |||||||
| High school diploma/GED or less | 716 (39.8) | 48.3 | 11.0 | <0.0001 | 0.86 | 0.85 | 0.001 |
| Some college | 546 (30.4) | 49.7 | 11.1 | 0.74 | 0.69 | ||
| College degree or higher | 536 (29.8) | 53.1 | 11.2 | 0.67 | 0.62 | ||
| % Federal Poverty Guidelines | |||||||
| <100% | 622 (34.6) | 49.4 | 11.9 | 0.03 | 0.80 | 0.84 | 0.66 |
| 100 to <200% | 795 (44.2) | 50.3 | 10.6 | 0.76 | 0.68 | ||
| 200 to <250% | 381 (21.2) | 51.3 | 11.6 | 0.74 | 0.71 | ||
| Food Securityf | |||||||
| High/marginal food security | 868 (48.8) | 51.0 | 11.6 | 0.004 | 0.73 | 0.68 | 0.04 |
| Low/very low food security | 912 (51.2) | 49.4 | 10.9 | 0.80 | 0.79 | ||
| Geographic Region | |||||||
| Northeast | 260 (14.5) | 50.7 | 11.0 | 0.03 | 0.64 | 0.60 | <0.001 |
| Midwest | 410 (22.8) | 49.6 | 11.1 | 0.80 | 0.78 | ||
| South | 818 (45.5) | 49.7 | 11.1 | 0.84 | 0.82 | ||
| West | 310 (17.2) | 51.7 | 12.1 | 0.65 | 0.53 | ||
30 day Prime Diet Quality Score (PDQS-30), possible scores range from 0–126.
p-value from one-way ANOVA
p-value from Kruskall-Wallis nonparametric test for differences in means
Includes participants identifying as Middle Eastern/North African
Includes participants identifying as Asian (A, n=26), Native Hawaiian/Other Pacific Islander (NHPI, n=4), American Indian/Alaska Native (AIAN, n=19), Multiracial/Multiethnic (M, n=44), and other races (O, n=18) as self-described.
n=18 missing due to self-reported unknown food security status
In the study population, 41% of adults agreed that they make dietary choices that are good for the environment, and these choices differed by age (p<.001), gender (p=0.01), race and ethnicity (p=0.001), education (p=0.002) and food security (p=0.03) (Table 2). Younger adults, women and gender-nonconforming persons, minoritized racial and ethnic groups, and those with higher education and with food insecurity were more likely to agree that they make dietary choices for the environment. Similarly, 35% of participants agreed that they make dietary choices to reduce their impact on climate change; this agreement level varied by age (p<.0001), gender (p=0.03), race and ethnicity (p<.0001), education (p=0.01), food security (p=0.03), and geographic region (p=0.046). Climate was a stronger motivator amongst young adults, women and gender-nonconforming persons, minoritized racial and ethnic groups, people with higher education levels, those with food insecurity, and adults living in the Northeastern US. About 64% of participants agreed that they make dietary choices that were good for health, and agreement level differed significantly by age (p=0.003), education (p<.0001), %FPG (p=0.04), and food security (p=0.002). Adults with older age, greater educational attainment, higher income, and food security more highly ranked health as a motivator for dietary choices.
Table 2.
Mean (SD) environmental, climate, and health-related motivation scores, stratified by sociodemographic characteristics, for 1798 US adults with lower incomes surveyed in December 2022.
| Sociodemographic Variable | n | I try to make food and beverage choices that… a | |||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Are good for the environment | Reduce my impact on climate change | Are good for my health | |||||||||||
|
| |||||||||||||
| % Agreeb | Mean | SD | P c | % Agreeb | Mean | SD | P c | % Agreeb | Mean | SD | P c | ||
| All participants | 1798 | 40.5 | 4.19 | 1.71 | 34.7 | 3.91 | 1.76 | 64.1 | 4.98 | 1.58 | |||
| Age (years) | |||||||||||||
| 18–29 | 328 | 45.1 | 4.48 | 1.70 | <0.001 | 39.6 | 4.23 | 1.69 | <.0001 | 62.5 | 4.94 | 1.57 | 0.003 |
| 30–39 | 358 | 43.0 | 4.31 | 1.71 | 39.9 | 4.09 | 1.76 | 60.6 | 4.98 | 1.54 | |||
| 40–49 | 330 | 40.3 | 4.23 | 1.70 | 33.9 | 3.96 | 1.76 | 61.5 | 4.83 | 1.66 | |||
| 50–59 | 307 | 35.5 | 3.97 | 1.71 | 27.7 | 3.64 | 1.78 | 61.2 | 4.83 | 1.65 | |||
| ≥60 | 475 | 38.7 | 4.03 | 1.71 | 32.2 | 3.69 | 1.77 | 71.6 | 5.21 | 1.50 | |||
| Gender | |||||||||||||
| Woman | 924 | 41.7 | 4.30 | 1.67 | 0.01 | 36.4 | 4.00 | 1.72 | 0.03 | 65.5 | 5.04 | 1.57 | 0.21 |
| Man | 858 | 39.2 | 4.07 | 1.75 | 32.4 | 3.80 | 1.80 | 62.8 | 4.91 | 1.60 | |||
| Gender non-conforming | 16 | 43.8 | 4.31 | 1.45 | 56.3 | 4.44 | 1.55 | 56.3 | 5.25 | 1.34 | |||
| Race and Ethnicity | |||||||||||||
| Non-Hispanic Black | 279 | 44.4 | 4.51 | 1.75 | 0.001 | 39.8 | 4.28 | 1.76 | <.0001 | 67.4 | 5.21 | 1.57 | 0.05 |
| Hispanic | 171 | 41.5 | 4.28 | 1.80 | 40.9 | 4.13 | 1.77 | 62.0 | 5.01 | 1.60 | |||
| Non-Hispanic Whited | 1237 | 39.2 | 4.09 | 1.69 | 32.6 | 3.78 | 1.75 | 63.2 | 4.92 | 1.58 | |||
| A/NHPI/AIAN/Me | 111 | 43.2 | 4.41 | 1.58 | 35.1 | 4.09 | 1.72 | 69.4 | 4.99 | 1.55 | |||
| Education | |||||||||||||
| HS Diploma/GED or less | 716 | 39.5 | 4.18 | 1.71 | 0.002 | 34.2 | 3.90 | 1.74 | 0.01 | 59.2 | 4.80 | 1.62 | <.0001 |
| Some college | 546 | 36.5 | 4.02 | 1.72 | 31.3 | 3.75 | 1.75 | 62.3 | 4.88 | 1.60 | |||
| College degree or higher | 536 | 45.9 | 4.38 | 1.70 | 38.6 | 4.07 | 1.79 | 72.6 | 5.32 | 1.46 | |||
| % Federal Poverty Guidelines | |||||||||||||
| <100% | 622 | 41.0 | 4.23 | 1.77 | 0.76 | 35.2 | 3.96 | 1.82 | 0.63 | 59.8 | 4.86 | 1.67 | 0.04 |
| 100 to <200% | 795 | 39.9 | 4.19 | 1.70 | 34.3 | 3.88 | 1.76 | 65.8 | 5.01 | 1.57 | |||
| 200 to <250% | 381 | 40.9 | 4.14 | 1.64 | 34.4 | 3.87 | 1.68 | 67.7 | 5.11 | 1.45 | |||
| Food Securityf | |||||||||||||
| High/marginal food security | 868 | 39.6 | 4.11 | 1.75 | 0.03 | 33.4 | 3.82 | 1.84 | 0.03 | 67.6 | 5.10 | 1.60 | 0.002 |
| Low/very low food security | 912 | 41.8 | 4.28 | 1.68 | 36.2 | 3.99 | 1.70 | 61.1 | 4.86 | 1.56 | |||
| Geographic Region | |||||||||||||
| Northeast | 260 | 41.2 | 4.34 | 1.70 | 0.38 | 39.2 | 4.18 | 1.76 | 0.046 | 69.2 | 5.11 | 1.59 | 0.53 |
| Midwest | 410 | 40.5 | 4.21 | 1.69 | 34.4 | 3.93 | 1.72 | 62.4 | 4.93 | 1.60 | |||
| South | 818 | 40.0 | 4.17 | 1.73 | 34.0 | 3.85 | 1.78 | 63.7 | 4.97 | 1.59 | |||
| West | 310 | 41.3 | 4.10 | 1.71 | 32.9 | 3.80 | 1.77 | 63.2 | 4.95 | 1.54 | |||
Participants were asked how much they agree with the statement “I try to make food and beverage choices that…are good for the environment, reduce my impact on climate change, are good for my health.” Responses were on a scale of 1–7, strongly disagree (1) to strongly agree (7).
Percent of participants reporting 5, 6, or 7 on scale of 1–7.
P-value for differences in means, results from one-way ANOVA
Includes participants identifying as Middle Eastern/North African
Includes participants identifying as Asian (A), Native Hawaiian/Other Pacific Islander (NHPI), American Indian/Alaska Native (AIAN), Multiracial/Multiethnic (M), and other races as self-described.
n=18 missing due to self-reported unknown food security status
Table 3 presents the association between environmental, climate, and health-related dietary motivations and dietary outcomes. In multivariate models, compared to those with neutral motivations, PDQS-30 scores were higher for participants who agreed that they make food and beverage choices that are good for the environment (β=2.28, CI=1.09, 3.47, p<.001), climate (β =2.15, CI=0.90, 3.40, p<.001), or health (β =5.27, CI=3.98, 6.56, p<.0001). PDQS-30 scores were lower for participants who disagreed that they make dietary choices for climate change (β =−1.34, CI=−2.57, −0.10, p=0.03) or health (β =−1.99, CI=−3.66, −0.31, p=0.02) when compared to those with neutral attitudes.
Table 3.
Associations between environmental, climate, and health-related dietary motivators and dietary intake frequency for 1798 US adults with lower incomes surveyed in December 2022.
| Dietary outcome | Motivation Classification (reference = neutral) | I try to make food and beverage choices that… a | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| Are good for the environmentb | Reduce my impact on climate changeb | Are good for my healthc | ||||||||
|
| ||||||||||
| βd | 95% CI | P | β d | 95% CI | P | β d | 95% CI | P | ||
| PDQS-30e | Agree | 2.28 | 1.09, 3.47 | <.001 | 2.15 | 0.90, 3.40 | <.001 | 5.27 | 3.98, 6.56 | <.0001 |
| Disagree | −0.93 | −2.24, 0.38 | 0.16 | −1.34 | −2.57, −0.10 | 0.03 | −1.99 | −3.66, −0.31 | 0.02 | |
| Dietary Intake Frequency (times/day) | FR f | 95% CI | P | FR f | 95% CI | P | FR f | 95% CI | P | |
| Red meat (unprocessed) | Agree | 0.89 | 0.79, 1.00 | 0.05 | 0.94 | 0.84, 1.07 | 0.35 | 0.98 | 0.86, 1.11 | 0.72 |
| Disagree | 0.90 | 0.79, 1.02 | 0.09 | 1.01 | 0.90, 1.14 | 0.82 | 1.01 | 0.86, 1.19 | 0.87 | |
| Processed red meat | Agree | 0.98 | 0.86, 1.11 | 0.77 | 1.03 | 0.90, 1.18 | 0.66 | 0.91 | 0.79, 1.04 | 0.18 |
| Disagree | 0.97 | 0.84, 1.11 | 0.65 | 0.99 | 0.87, 1.13 | 0.89 | 0.95 | 0.80, 1.14 | 0.60 | |
| Poultry (unprocessed) | Agree | 1.03 | 0.93, 1.15 | 0.54 | 0.96 | 0.85, 1.08 | 0.49 | 1.09 | 0.97, 1.23 | 0.15 |
| Disagree | 0.99 | 0.88, 1.12 | 0.90 | 0.95 | 0.85, 1.06 | 0.38 | 0.93 | 0.79, 1.08 | 0.33 | |
| Processed poultry | Agree | 1.15 | 1.01, 1.31 | 0.04 | 1.21 | 1.06, 1.39 | 0.006 | 0.81 | 0.70, 0.94 | 0.004 |
| Disagree | 0.95 | 0.82, 1.09 | 0.44 | 0.96 | 0.84, 1.10 | 0.59 | 1.02 | 0.85, 1.23 | 0.82 | |
| Fish | Agree | 1.41 | 1.24, 1.61 | <.0001 | 1.28 | 1.12, 1.48 | <.001 | 1.19 | 1.03, 1.37 | 0.02 |
| Disagree | 0.70 | 0.61, 0.81 | <.0001 | 0.79 | 0.69, 0.90 | <.001 | 0.98 | 0.82, 1.18 | 0.82 | |
| Fruits and vegetables | Agree | 1.14 | 1.05, 1.25 | 0.003 | 1.14 | 1.04, 1.25 | 0.006 | 1.31 | 1.19, 1.44 | <.0001 |
| Disagree | 0.91 | 0.83, 1.01 | 0.07 | 0.94 | 0.85, 1.03 | 0.15 | 0.96 | 0.85, 1.09 | 0.54 | |
| Plant Proteinsg | Agree | 1.24 | 1.10, 1.40 | <.001 | 1.19 | 1.05, 1.34 | 0.006 | 1.24 | 1.09, 1.41 | <.001 |
| Disagree | 0.95 | 0.84, 1.09 | 0.48 | 0.85 | 0.75, 0.96 | 0.009 | 1.05 | 0.89, 1.24 | 0.58 | |
Participants were asked how much they agree with the statement “I try to make food and beverage choices that…are good for the environment, reduce my impact on climate change, are good for my health.” Responses were on a scale of 1–7, strongly disagree (1) to strongly agree (7). Participants were classified as agree (response of 5–7), neutral (response of 4), or disagree (response of 1–3), with neutral as the reference group.
Model adjusted for age, gender, race and ethnicity, education, % Federal Poverty Guidelines, food security, and health motivations
Model adjusted for age, gender, race and ethnicity, education, % Federal Poverty Guidelines, food security, and environmental motivations
Results from a generalized linear model with an identity link and normal distribution, to account for normal distribution of PDQS-30
30 day Prime Diet Quality Score (PDQS-30), possible scores range from 0–126.
Results from a generalized liner model with a log link and gamma distribution, to account for positive skewed distribution of dietary intake frequency variables. FR = Frequency Ratio. 100(FR-1) = % higher intake compared to neutral response.
Sum of nuts/seeds and beans/peas/soy intake frequency
Participants who agreed with the statement “I try to make food and beverage choices that are good for the environment” had 15% higher intake frequency of processed poultry (p=0.04), 41% higher intake frequency of fish (p<.0001), 14% higher intake frequency of fruits and vegetables (p=0.003), and 24% higher intake frequency of plant proteins (p<.001) compared to those with neutral responses (Table 3). Those motivated by climate had 21% higher processed poultry intake frequency (p=0.006), 28% higher fish intake frequency (p<.001), 14% higher fruit and vegetable intake frequency (p=0.006), and 19% higher plant protein intake frequency (p=0.006) compared with those with neutral responses. Those who disagreed that they make choices for the environment had 30% lower intake frequency of fish (p<.0001), while those who disagreed that they make choices for climate had 21% lower intake frequency of fish (p<.001) and 15% lower intake frequency of plant proteins (p=0.009) than participants with neutral responses. Participants who agreed with the statement “I try to make food and beverage choices that are good for my health” had 19% lower intake frequency of processed poultry (p=0.004), 19% higher intake frequency of fish (p=0.02), 31% higher intake frequency of fruits and vegetables (p<.0001), and 24% higher intake frequency of plant proteins (p<.001) than those with neutral responses.
Mean ranking of the effectiveness of different climate mitigation behaviors in this population is displayed in Table 4. Recycling was rated by participants as the most effective behavior (mean=3.4), followed by “use less plastic” and “save energy at home” (means = 3.3). Eating less meat was ranked as the lowest (mean=2.4) compared to all other climate mitigation behaviors (p’s<0.0001). Diet-related climate mitigation behaviors had the highest percentage of “don’t know” responses (11–13%).
Table 4.
Mean ranking of the effectiveness of different climate mitigation behaviors for a national sample of US adults with lower incomes, surveyed in December 2022a
| Climate mitigation behavior | Meanb | SD | n | p-valuec | Don’t knowd (%) |
|---|---|---|---|---|---|
|
| |||||
| Eat less meat | 2.4 | 1.1 | 1600 | ref | 11.0 |
| Eat organic foods | 2.5 | 1.1 | 1572 | <.0001 | 12.6 |
| Eat local, seasonal foods | 2.9 | 1.0 | 1600 | <.0001 | 11.0 |
| Drive less | 3.1 | 1.0 | 1677 | <.0001 | 6.7 |
| Use less plastic | 3.3 | 1.0 | 1697 | <.0001 | 5.6 |
| Save energy at home | 3.3 | 0.9 | 1694 | <.0001 | 5.8 |
| Recycle | 3.4 | 0.9 | 1708 | <.0001 | 5.0 |
Participants were asked to indicate whether they think each behavior is an effective way of combatting climate change (response ranged from 1=not effective, to 4= highly effective, 5= don’t know). Response options were displayed in random order.
Responses of “don’t know” were excluded from statistical analyses.
P-value for Wilcoxon signed-rank nonparametric test for within-individual comparison
Percentage of participants responding as “don’t know” for each mitigation behavior
Discussion
American adults with lower incomes reported making food and beverage choices that are good for the environment (41%), reduce impact on climate change (35%), or are good for health (64%). Agreement with environmental, climate or health-related dietary motivations was associated with higher diet quality scores when compared with neutral ranking. Compared with neutral rating, agreement with environmental, climate or health motivations was associated with higher intake frequencies of fish, fruits and vegetables, and plant proteins, but not with lower intake frequencies of red and processed meats. Additionally, processed poultry intake frequency was significantly higher for those motivated by the environment and climate change. Of several possible climate mitigation behaviors presented, participants perceived meat reduction as least effective. These results suggest that dietary choices of individuals with lower incomes are in part motivated by environment, climate, and health concerns, yet the role of red and processed meat in these outcomes may be underestimated.
Evidence of higher dietary quality with higher environmental valuation has been observed in previous studies. Valuation of sustainable foods and sustainable food practices has been associated with better diet quality in young adults,40, 41 and environmental and climate motivations have been associated with lower red meat intake frequency among university students.25 A large survey recently conducted in Italy determined that participants who reported that climate change is an urgent environmental problem had lower intake frequency of beef and pork, but not chicken or processed meat.26 In the current study, agreement with making dietary choices for the environment, climate, or health was associated with higher intake frequency of plant proteins, possibly reflecting increasing accessibility, affordability, or acceptability of these protein types.19
Counter to the study hypothesis, none of the dietary motivations were significantly associated with lower frequency of red and processed meat intake in this study. This may be due, in part, to the low perceived effectiveness of eating less meat for combating climate change relative to other behaviors such as recycling, whereas research shows that eating a completely plant-based diet to be four times more effective than recycling.42 Consistent with the current findings, it is well documented that consumers underestimate the environmental impact of food,23 and meat consumption in particular.21, 23, 25, 43 Additionally, there are mixed messages in the US about the health benefits and risks of red meat intake44 and saturated fat.45 It also may be engrained in many Americans that meat is essential to a healthy diet. In a previous study, primary reasons for consuming meat were beliefs that a healthy diet includes meat and that a meal is incomplete without meat.24 Furthermore, the popularity of meat-heavy diets such as the Keto and Paleo diets46 may confuse consumers as to the health impacts of red and processed meat. Findings from the current study suggest that, like the population overall, US adults with lower incomes may in part be confused about the health and environmental impacts of red and processed meat consumption, but it is also likely that other factors, such as cost and availability, food and marketing environments, food preferences, and cultural norms around the importance of red and processed meat consumption affect choices in this population.21, 24
A previous review of the literature concluded that sustainability is not highly considered when making food choices,23 yet the current study demonstrates that the environment, climate change, and health can motivate dietary choices of adults with lower incomes. The changing environment affects food availability and helps shape attitudes towards sustainability; as climate change and other human-environment disruptions affect food systems, environmental perceptions and dietary motivations may shift.13, 47 For example, there is recent evidence that the COVID-19 pandemic, possibly due to changes in food system functioning, corresponded with increased interest in sustainable diets in Europe.48
Previously, the environment, climate and health were also shown to motivate dietary choices in young adults.25 Younger adults in the current study more highly ranked the importance of the environment and climate in dietary choices. Climate anxiety persists in young people around the world;49 therefore efforts to promote sustainable dietary choices among younger adults might be more effective and result in long-term behavior change. The current results also underscore that, given underestimation of the importance of red meat in the climate impact of dietary choices, there is a role for public health messaging and education around this topic to support such behavior change.
Sociodemographic differences in environmental and climate dietary motivations track with concerns of environmental health risks in the US. Non-Hispanic Black and other minoritized races, females, and higher educated groups in the US showed stronger perceptions of environmental health risks.50 Similarly, Hispanic/Latino and African American groups were more likely to be alarmed or concerned about climate change than White groups.51 Greater environmental concern may reflect perceptions of vulnerability52 and personal experiences, such as inequities in environmental risks;53, 54 furthermore, social problems might be observed through an environmental justice lens in some groups that have been economically and socially marginalized.17 Lastly, environmental and climate change concerns of lower income and historically marginalized racial and ethnic groups may be underestimated.55 This study reiterates the need to ensure that policies and programs for sustainable eating are inclusive of historically underrecognized populations.
While herein environmental, climate and health-based dietary motivations are associated with some components of healthy diets, it is possible that these associations may be underestimated as barriers may prevent translation of environmental and dietary motivations to behaviors.56, 57 Both external factors (economic, social, cultural, lack of infrastructure, convenience) and internal factors (motivation, education, values, emotional involvement) can be barriers to pro-environmental behavior,56, 58 and dietary behavior,59–62 as well as drivers of food choice, possibly affecting sustainable eating and the associations between motivations and dietary intake. Consumers often view sustainable diets as inaccessible, inconvenient and expensive,23 and this may be especially true for lower-income households.8 Neighborhoods where economically disadvantaged populations reside reportedly have a greater prevalence of fast food and convenience stores, which promote unhealthy diets63, 64 and may affect access to healthy plant-based foods.
Secondly, actions may not always track to the most effective choices for health or the environment. This may in part be to lack of consumer knowledge and information regarding the most healthful and environmentally conscious choices (as may be the case with red and processed meat intake), but also perceptions about healthfulness,65, 66 environmental claims of products,67 and the resulting “health halo” stemming from corporate social responsibility (CSR) marketing.68 For example, in a recent study, positive framing of climate-friendly fast food menu choices influenced perceived healthfulness of choices.69 Such health halos and greenwashing – the act of conveying misleading information regarding environmental practices70 – may confuse consumers, particularly when combined with perceived effectiveness of climate reduction behaviors. These effects can reach beyond individual impacts on climate change and potentially impact public support for climate-friendly policies. Additionally, consumer perceptions and purchasing power may reinforce CSR marketing and contribute to the effectiveness of corporate greenwashing.70
Lastly, a plant-based diet or lower red meat intake does not necessarily equate to a healthy diet or health benefits.20 For example, previous studies have shown that benefits of plant-based diets were observed with healthy plant-based diets (e.g., high fruits and vegetables, nuts, and whole grains, but low in refined grains, added sugars, and potatoes) but not unhealthy plant-based diets.6 This is important to consider as populations shift to plant-based diets, particularly in under-resourced communities where access to healthy plant-based foods may be limited.
Plant-based diets, particularly those low in red and processed meat, are recommended for human and environmental health2, 7, but rising costs of meats with climate change71 may provide an opportunity to address affordable and sustainable healthy diets in higher-income countries such as the US.72 It has been predicted that even in developed countries, increasing food prices due to climate change may necessitate shifts to lower cost foods, particularly among groups with lower incomes.73 There is a need to support such communities vulnerable to the double-burden of climate change and negative food environments. Educational programming may increase knowledge of environmentally friendly choices while improving dietary quality,74 but more research is needed in economically and socially marginalized populations to understand the multi-factorial and structural barriers to adopting more sustainable diets. Individual and community-based intervention programs have been effective at improving diet quality in populations with lower incomes,59 and such programs could expand to sustainable eating. Food labeling may also be effective in supporting sustainable dietary choices, but must be aligned with health goals.69 Sustainability-focused food labels must also be understandable to consumers, and convey information without causing confusion or information overload.75, 76 Ultimately governing bodies, food processors, retailers, and servicers should be involved to create change.2 Institutions such as public schools, hospitals, and government buildings have potential to implement sustainable food practices,77 environmental sustainability should be included in federal and individual dietary guidelines78 and institutional procurement policies, and plant-based foods should be subsidized while taxing77 or lifting subsidies on foods with high GHGE. To the extent possible, policies that improve the sustainability of the food offered (e.g., shifting the default options or increasing the ratio of plant-based entrees to red meat entrees) should be prioritized. Doing so will help facilitate more sustainable food choices without placing the burden on the consumer to make the more sustainable choice. Lastly, there should be continued focus on improving the food environment for socioeconomically disadvantaged populations so that healthy plant-based foods are convenient and accessible.
This study has several limitations. It is a cross-sectional study, and therefore causal inferences cannot be made. Data were self-reported, which may be subject to recall bias and social desirability bias.79 However, participants were blinded to the research hypothesis which may minimize social desirability bias. Selection bias may have occurred if panel members differed from non-responders with respect to beliefs and actions. It is possible that due to the method of recruitment, this study population might be more tech savvy or highly educated,80 and thus the population might not be representative of the lower-income US population in all aspects. The survey was also presented only in English, which may have limited participation of non-English speaking persons. Data collected via online participant panels may be prone to providing quick “good enough” answers rather than thoughtful answers.80 It is likely that such bias in this study would underestimate the observed effects. Furthermore, this limitation was minimized through use of attention checks and screening for unrealistically-short survey completion times. Small numbers of participants falling into some groups, such as gender non-conforming persons and people identifying as races other than Black, Hispanic, and White did not allow for meaningful interpretation of associations within these groups; future studies of diverse populations are important to further evaluate the observed associations. A dietary screener was used to capture dietary patterns which may not capture all nuances of a healthy diet; it may be helpful for future studies to consider additional dietary indices that more directly align with the Dietary Guidelines for Americans,7 such as the Healthy Eating Index.81 Lastly, there are many potential factors influencing food choices such as taste preferences, cultural norms, culinary skills, access, and price that were not measured in this study.82, 83 These influences may serve as potential confounders, or may result in disconnect between motivations and dietary intake and are thus an important area of future research.
Conclusions
Among US adults with lower incomes, environmental, climate, and health-related dietary motivations were associated with higher diet quality scores and higher intake frequency of some healthy dietary components after controlling for sociodemographic variables. Counter to the hypothesis, these motivations were not associated with intake frequency of red and processed red meat. Environmental and climate motivations were higher for women and people identifying as gender-nonconforming, people from historically minoritized racial and ethnic groups, those with higher education, and people with low or very low food security. Understanding sociodemographic differences in dietary motivations and how such motivations are associated with dietary food group intake frequency lays the foundation for supporting sustainable dietary behaviors in underserved populations. Recognizing and cultivating such motivations in these populations presents opportunities to support healthy diets, improve health, and reduce environmental impacts while advancing transformative adaptation to climate change.
Research Snapshot.
Research Question:
How are environmental perceptions and dietary motivations associated with dietary intake frequency of different food groups in US adults with lower incomes?
Key Findings:
In this cross-sectional study of 1,798 US adults with lower-incomes, those who reported that their dietary choices were motived by the environment, climate, or health had significantly higher diet quality scores, and higher intake frequency of fish, fruits and vegetables, and plant proteins compared to those with neutral motivations. Motivations were not associated with red and processed meat intake frequency, and reducing meat intake was perceived as minimally effective as a climate mitigation strategy.
Funding/Financial Disclosure:
CWL and MJS and research supported by The University of Michigan Office of Research. JF was supported by the National Institute of Diabetes and Digestive and Kidney Diseases of the National Institutes of Health (Award Number K01DK113068). JAW was supported by the National Institutes of Diabetes and Digestive and Kidney Diseases of the National Institutes of Health (Award #K01DK119166). The content is solely the responsibility of the authors and does not necessarily represent the official views of the National Institutes of Health. The authors have no financial disclosures.
Footnotes
Conflicts of Interest: None
Contributor Information
Melissa J. Slotnick, Department of Nutritional Sciences, The University of Michigan School of Public Health, 1415 Washington Heights, SPH I, Ann Arbor, MI 48109, USA.
Jennifer Falbe, Department of Human Ecology, University of California Davis, Davis, CA, 95616, USA.
Julia A. Wolfson, Department of International Health, Johns Hopkins Bloomberg School of Public Health, Baltimore, MD, 21205, USA, Department of Health Policy and Management, Johns Hopkins Bloomberg School of Public Health, Baltimore, MD, 21205, USA.
Andrew D. Jones, Department of Nutritional Sciences, The University of Michigan School of Public Health, Ann Arbor, MI, 48108, USA.
Cindy W. Leung, Department of Nutrition, Harvard T.H. Chan School of Public Health, Boston, MA 02115, USA.
References
- 1.IPCC. Summary for Policymakers. In: Climate Change 2023: Synthesis Report. A Report of the Intergovernmental Panel on Climate Change. Contribution of Working Groups I, II and III to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, Lee H and Romero J (eds.)]. Geneva, Switzerland: IPCC; 2023. [Google Scholar]
- 2.Willett W, Rockström J, Loken B, et al. Food in the Anthropocene: the EAT–Lancet Commission on healthy diets from sustainable food systems. The Lancet. 2019;393:447–492. [DOI] [PubMed] [Google Scholar]
- 3.Poore J, Nemecek T. Reducing food’s environmental impacts through producers and consumers. Science. 2018;360:987–992. [DOI] [PubMed] [Google Scholar]
- 4.Tilman D, Clark M. Global diets link environmental sustainability and human health. Nature. 2014;515:518–522. [DOI] [PubMed] [Google Scholar]
- 5.Clark M, Springmann M, Rayner M, et al. Estimating the environmental impacts of 57,000 food products. Proceedings of the National Academy of Sciences. 2022;119:e2120584119. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Hemler EC, Hu FB. Plant-based diets for personal, population, and planetary health. Advances in Nutrition. 2019;10:S275–S283. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.USDA. Dietary Guidelines for Americans, 2020–2025. 9th ed2020.
- 8.Leiserowitz A, Ballew M, Rosenthal S, Seamaan J. Climate change and the American diet. New Haven, CT: Yale University and Earth Day Network; 2020. [Google Scholar]
- 9.Frank SM, Taillie LS, Jaacks LM. How Americans eat red and processed meat: an analysis of the contribution of thirteen different food groups. Public Health Nutrition. 2022;25:1406–1415. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Zeng L, Ruan M, Liu J, et al. Trends in processed meat, unprocessed red meat, poultry, and fish consumption in the United States, 1999–2016. Journal of the Academy of Nutrition and Dietetics. 2019;119:1085–1098. e1012. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Rose D, Willits-Smith AM, Heller MC. Single-item substitutions can substantially reduce the carbon and water scarcity footprints of US diets. The American journal of clinical nutrition. 2022;115:378–387. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12.Gamble JL, Balbus J, Berger M, et al. THE IMPACTS OF CLIMATE CHANGE ON HUMAN HEALTH IN THE UNITED STATES A Scientific Assessment. US Global Change Resarch Program. 2016. [Google Scholar]
- 13.Fanzo J, Bellows AL, Spiker ML, Thorne-Lyman AL, Bloem MW. The importance of food systems and the environment for nutrition. The American Journal of Clinical Nutrition. 2021;113:7–16. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.USDA. Economic Research Service Food Price Outlook. Vol 2023.
- 15.Green R, Cornelsen L, Dangour AD, et al. The effect of rising food prices on food consumption: systematic review with meta-regression. Bmj. 2013;346. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Bublitz MG, Catlin JR, Jones AC, Lteif L, Peracchio LA. Plant power: SEEDing our future with plant‐based eating. Journal of Consumer Psychology. 2023;33:167–196. [Google Scholar]
- 17.Song H, Lewis NA Jr, Ballew MT, et al. What counts as an “environmental” issue? Differences in issue conceptualization by race, ethnicity, and socioeconomic status. Journal of Environmental Psychology. 2020;68:101404. [Google Scholar]
- 18.Burt KG, Fera J, Lewin-Zwerdling A. Differences in US Adults’ Value of and Preferences for Sustainable Food by Race/ethnicity, Income, and Education. Journal of Hunger & Environmental Nutrition. 2021;16:321–335. [Google Scholar]
- 19.Macdiarmid J The food system and climate change: are plant-based diets becoming unhealthy and less environmentally sustainable? Proceedings of the nutrition society. 2022;81:162–167. [DOI] [PubMed] [Google Scholar]
- 20.Hemler EC, Hu FB. Plant-based diets for cardiovascular disease prevention: all plant foods are not created equal. Current atherosclerosis reports. 2019;21:1–8. [DOI] [PubMed] [Google Scholar]
- 21.Sanchez-Sabate R, Badilla-Briones Y, Sabate J. Understanding attitudes towards reducing meat consumption for environmental reasons. A qualitative synthesis review. Sustainability. 2019;11:6295. [Google Scholar]
- 22.Sánchez LA, Roa-Díaz ZM, Gamba M, et al. What Influences the Sustainable Food Consumption Behaviours of University Students? A Systematic Review. International journal of public health. 2021;66. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.van Bussel L, Kuijsten A, Mars M, van’t Veer P. Consumers’ perceptions on food-related sustainability: A systematic review. Journal of Cleaner Production. 2022:130904. [Google Scholar]
- 24.Neff RA, Edwards D, Palmer A, Ramsing R, Righter A, Wolfson J. Reducing meat consumption in the USA: a nationally representative survey of attitudes and behaviours. Public health nutrition. 2018;21:1835–1844. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Slotnick MJ, Falbe J, Cohen JF, Gearhardt AN, Wolfson JA, Leung CW. Environmental and climate impact perceptions in university students: Sustainability motivations and perceptions correspond with lower red meat intake. Journal of the Academy of Nutrition and Dietetics. 2022. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26.Bimbo F Climate change-aware individuals and their meat consumption: Evidence from Italy. Sustainable Production and Consumption. 2023. [Google Scholar]
- 27.Grummon AH, Musicus AA, Salvia MG, Thorndike AN, Rimm EB. Impact of Health, Environmental, and Animal Welfare Messages Discouraging Red Meat Consumption: An Online Randomized Experiment. Journal of the Academy of Nutrition and Dietetics. 2022. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Taillie LS, Prestemon CE, Hall MG, Grummon AH, Vesely A, Jaacks LM. Developing health and environmental warning messages about red meat: An online experiment. Plos one. 2022;17:e0268121. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.USDHHS. Annual Update of the HHS Poverty Guidelines. Vol 87 FR 3315. 2022–01166 ed: Department of Health and Human Services; 2022:3315–3316. [Google Scholar]
- 30.Slotnick MJ, Leung CW. Water Insecurity Indicators Are Associated with Lower Diet and Beverage Quality in a National Survey of Lower-Income United States Adults. The Journal of Nutrition. 2023. [DOI] [PubMed] [Google Scholar]
- 31.Chandler J, Rosenzweig C, Moss AJ, Robinson J, Litman L. Online panels in social science research: Expanding sampling methods beyond Mechanical Turk. Behavior research methods. 2019;51:2022–2038. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Gicevic S, Mou Y, Bromage S, Fung TT, Willett W. Development of a diet quality screener for global use: Evaluation in a sample of US women. Journal of the Academy of Nutrition and Dietetics. 2021;121:854–871. e856. [DOI] [PubMed] [Google Scholar]
- 33.Fung TT, Isanaka S, Hu FB, Willett WC. International food group–based diet quality and risk of coronary heart disease in men and women. The American journal of clinical nutrition. 2018;107:120–129. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.de Boer J, de Witt A, Aiking H. Help the climate, change your diet: A cross-sectional study on how to involve consumers in a transition to a low-carbon society. Appetite. 2016;98:19–27. [DOI] [PubMed] [Google Scholar]
- 35.Bureau USC. About the topic of race: United States Government; 2022. [Google Scholar]
- 36.USDA. Food Security in the US Survey Tools. Vol 2022: U.S. Department of Agriculture Economic Research Service; 2022. [Google Scholar]
- 37.Guenther PM, Jensen HH, Batres-Marquez SP, Chen C-F. Sociodemographic, knowledge, and attitudinal factors related to meat consumption in the United States. Journal of the American Dietetic Association. 2005;105:1266–1274. [DOI] [PubMed] [Google Scholar]
- 38.Wang DD, Leung CW, Li Y, et al. Trends in dietary quality among adults in the United States, 1999 through 2010. JAMA internal medicine. 2014;174:1587–1595. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.SAS. Version 9.4. SAS Institute, Inc. Cary, NC: 2013. [Google Scholar]
- 40.Larson N, Laska MN, Neumark-Sztainer D. Do young adults value sustainable diet practices? Continuity in values from adolescence to adulthood and linkages to dietary behaviour. Public health nutrition. 2019;22:2598–2608. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Pelletier JE, Laska MN, Neumark-Sztainer D, Story M. Positive attitudes toward organic, local, and sustainable foods are associated with higher dietary quality among young adults. Journal of the Academy of Nutrition and Dietetics. 2013;113:127–132. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42.Wynes S, Nicholas KA. The climate mitigation gap: education and government recommendations miss the most effective individual actions. Environmental Research Letters. 2017;12:074024. [Google Scholar]
- 43.Hartmann C, Siegrist M. Consumer perception and behaviour regarding sustainable protein consumption: A systematic review. Trends in Food Science & Technology. 2017;61:11–25. [Google Scholar]
- 44.Qian F, Riddle MC, Wylie-Rosett J, Hu FB. Red and processed meats and health risks: how strong is the evidence? Diabetes Care. 2020;43:265–271. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45.Liu AG, Ford NA, Hu FB, Zelman KM, Mozaffarian D, Kris-Etherton PM. A healthy approach to dietary fats: understanding the science and taking action to reduce consumer confusion. Nutrition journal. 2017;16:1–15. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46.Basile A Popularity of Commercial and Non-Commercial Diets From 2010–2020: A Google Trends Analysis. Current Developments in Nutrition. 2021;5:391–391. [Google Scholar]
- 47.Marlon JR, Wang X, Bergquist P, et al. Change in US state-level public opinion about climate change: 2008–2020. Environmental Research Letters. 2022;17:124046. [Google Scholar]
- 48.Portugal-Nunes C, Cheng L, Briote M, Saraiva C, Nunes FM, Gonçalves C. COVID-19 changes public awareness about food sustainability and dietary patterns: a google trends analysis. Nutrients. 2022;14:4898. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49.Hickman C, Marks E, Pihkala P, et al. Climate anxiety in children and young people and their beliefs about government responses to climate change: a global survey. The Lancet Planetary Health. 2021;5:e863–e873. [DOI] [PubMed] [Google Scholar]
- 50.Shin M, Werner AK, Strosnider H, Hines LB, Balluz L, Yip FY. Public perceptions of environmental public health risks in the United States. International journal of environmental research and public health. 2019;16:1045. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 51.Ballew M, Maibach E, Kotcher J, et al. Which racial/ethnic groups care most about climate change. Yale Program on Climate Change Communication. 2020. [Google Scholar]
- 52.Satterfield TA, Mertz C, Slovic P. Discrimination, vulnerability, and justice in the face of risk. Risk analysis: An international journal. 2004;24:115–129. [DOI] [PubMed] [Google Scholar]
- 53.Mohai P, Pellow D, Roberts JT. Environmental justice. Annual review of environment and resources. 2009;34:405–430. [Google Scholar]
- 54.Abi Deivanayagam T, English S, Hickel J, et al. Envisioning environmental equity: climate change, health, and racial justice. The Lancet. 2023. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55.Pearson AR, Schuldt JP, Romero-Canyas R, Ballew MT, Larson-Konar D. Diverse segments of the US public underestimate the environmental concerns of minority and low-income Americans. Proceedings of the National Academy of Sciences. 2018;115:12429–12434. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 56.Wyss AM, Knoch D, Berger S. When and how pro-environmental attitudes turn into behavior: The role of costs, benefits, and self-control. Journal of environmental psychology. 2022;79:101748. [Google Scholar]
- 57.Pechey R, Monsivais P. Socioeconomic inequalities in the healthiness of food choices: Exploring the contributions of food expenditures. Preventive medicine. 2016;88:203–209. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58.Kollmuss A, Agyeman J. Mind the gap: why do people act environmentally and what are the barriers to pro-environmental behavior? Environmental education research. 2002;8:239–260. [Google Scholar]
- 59.Ziso D, Chun OK, Puglisi MJ. Increasing Access to Healthy Foods through Improving Food Environment: A Review of Mixed Methods Intervention Studies with Residents of Low-Income Communities. Nutrients. 2022;14:2278. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Ver Ploeg M, Dutko P, Breneman V. Measuring food access and food deserts for policy purposes. Applied Economic Perspectives and Policy. 2015;37:205–225. [Google Scholar]
- 61.Wolfson JA, Ramsing R, Richardson CR, Palmer A. Barriers to healthy food access: Associations with household income and cooking behavior. Preventive medicine reports. 2019;13:298–305. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 62.van der Heijden A, Te Molder H, Jager G, Mulder BC. Healthy eating beliefs and the meaning of food in populations with a low socioeconomic position: A scoping review. Appetite. 2021;161:105135. [DOI] [PubMed] [Google Scholar]
- 63.Hilmers A, Hilmers DC, Dave J. Neighborhood disparities in access to healthy foods and their effects on environmental justice. American journal of public health. 2012;102:1644–1654. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 64.Larson NI, Story MT, Nelson MC. Neighborhood environments: disparities in access to healthy foods in the US. American journal of preventive medicine. 2009;36:74–81. e10. [DOI] [PubMed] [Google Scholar]
- 65.Williams P Consumer understanding and use of health claims for foods. Nutrition reviews. 2005;63:256–264. [DOI] [PubMed] [Google Scholar]
- 66.Plasek B, Lakner Z, Temesi Á. Factors that influence the perceived healthiness of food. Nutrients. 2020;12:1881. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 67.Szabo S, Webster J. Perceived greenwashing: the effects of green marketing on environmental and product perceptions. Journal of Business Ethics. 2021;171:719–739. [Google Scholar]
- 68.Peloza J, Ye C, Montford WJ. When companies do good, are their products good for you? How corporate social responsibility creates a health halo. Journal of Public Policy & Marketing. 2015;34:19–31. [Google Scholar]
- 69.Wolfson JA, Musicus AA, Leung CW, Gearhardt AN, Falbe J. Effect of Climate Change Impact Menu Labels on Fast Food Ordering Choices Among US Adults: A Randomized Clinical Trial. JAMA Network Open. 2022;5:e2248320–e2248320. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 70.Wu Y, Zhang K, Xie J. Bad greenwashing, good greenwashing: Corporate social responsibility and information transparency. Management Science. 2020;66:3095–3112. [Google Scholar]
- 71.Godde CM, Mason-D’Croz D, Mayberry D, Thornton PK, Herrero M. Impacts of climate change on the livestock food supply chain; a review of the evidence. Global food security. 2021;28:100488. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 72.Springmann M, Clark MA, Rayner M, Scarborough P, Webb P. The global and regional costs of healthy and sustainable dietary patterns: a modelling study. The Lancet Planetary Health. 2021;5:e797–e807. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 73.Lake IR, Hooper L, Abdelhamid A, et al. Climate change and food security: health impacts in developed countries. Environmental health perspectives. 2012;120:1520–1526. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 74.Malan H, Amsler Challamel G, Silverstein D, et al. Impact of a scalable, multi-campus “Foodprint” seminar on college students’ dietary intake and dietary carbon footprint. Nutrients. 2020;12:2890. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 75.Asioli D, Aschemann-Witzel J, Nayga RM Jr. Sustainability-related food labels. Annual Review of Resource Economics. 2020;12:171–185. [Google Scholar]
- 76.Temple NJ, Fraser J. Food labels: a critical assessment. Nutrition. 2014;30:257–260. [DOI] [PubMed] [Google Scholar]
- 77.Bell BM. The climate crisis is here: a primer and call to action for public health nutrition researchers and practitioners in high-income countries. Public Health Nutrition. 2023;26:496–502. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 78.Rose D, Heller MC, Roberto CA. Position of the Society for Nutrition Education and Behavior: the importance of including environmental sustainability in dietary guidance. Journal of nutrition education and behavior. 2019;51:3–15. e11. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 79.Vesely S, Klöckner CA. Social desirability in environmental psychology research: three meta-analyses. Frontiers in Psychology. 2020;11:1395. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 80.Beto JA, Metallinos-Katsaras E, Leung C. Crowdsourcing: A Critical Reflection on This New Frontier of Participant Recruiting in Nutrition and Dietetics Research. Journal of the Academy of Nutrition and Dietetics. 2020;120:193–196. [DOI] [PubMed] [Google Scholar]
- 81.Shams-White MM, Pannucci TE, Lerman JL, et al. Healthy Eating Index-2020: Review and Update Process to Reflect the Dietary Guidelines for Americans, 2020–2025. Journal of the Academy of Nutrition and Dietetics. 2023. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 82.Larson N, Story M. A review of environmental influences on food choices. Annals of Behavioral Medicine. 2009;38:s56–s73. [DOI] [PubMed] [Google Scholar]
- 83.Leng G, Adan RA, Belot M, et al. The determinants of food choice. Proceedings of the Nutrition Society. 2017;76:316–327. [DOI] [PubMed] [Google Scholar]
