Adam Drewnowski
Zach Conrad- 1Center for Public Health Nutrition, University of Washington, Seattle, WA, United States
- 2Department of Kinesiology, William & Mary, Williamsburg, VA, United States
- 3Global Research Institute, William & Mary, Williamsburg, VA, United States
Introduction: Sustainable foods need to be nutrient-rich, affordable, environmentally friendly, and socially acceptable. Pulses, which include beans, lentils, chickpeas, and dried peas are a food group that can fit all those criteria.
Methods: These concepts were tested serially using nutrient profiling methods that focused on protein and were extended to include food prices, greenhouse gas emissions, and energy demand. The present sustainability analyses were based on the US Department of Agriculture (USDA) nutrient composition and food prices data. Environmental impact data came from life cycle assessments (LCA). First, the USDA Protein Foods Group was disaggregated into animal and plant proteins. Plant proteins were separated into pulses, soy products, and nuts and seeds.
Results: Pulses were among the lowest-cost protein sources (per 100 g and per 100 kcal) and had the lowest greenhouse gas emissions GHGE and energy demand. Pulses were among the most sustainable foods when monetary and energy costs were expressed per 50 g of protein (equivalent to 100% DV). Pulses scored well on the Nutrient Rich Food (NRF9.3) nutrient profiling system and on the related Affordable Nutrition Index that assessed nutrient density per penny.
Discussion: Pulses are a source of low-cost plant-based protein and a variety of priority vitamins and minerals, have low carbon footprint and energy demand, and are a valued culinary ingredient across diverse regions and cultures. As dietary guidance turns to plant-based diets, pulses need to be integrated into the global sustainability framework.
1 Introduction
Plant-based foods and plant-forward diets offer the promise of improved nutrition, greater affordability, and lower environmental footprint as compared to some existing diets (1–3). Several high-income countries are currently aiming to reduce the consumption of animal foods and so lower the dietary animal protein-to-plant protein ratio (4). The stated goal is to increase the proportion of plant proteins from the current value of approximately 33% of total protein intakes to 50% plant protein (5), 60% plant protein (6), or even beyond (7). Such initiatives are being promoted by researchers (1), consumer groups (8), foundations (9), and by some national and local governments (10, 11). The influential EAT-Lancet planetary health diet, designed for the globe, is built around whole grains, fruits, vegetables, nuts, and legumes and is 64% plant-protein based. The 2,500 kcal/day version restricts beef and pork to 7 g/day each but allows up to 50 g/day of dry beans, lentils, and peas (1).
Pulses, which include dry beans, lentils, peas, and chickpeas are excellent sources of plant-based protein, provide high-quality carbohydrates, are low in saturated fat and contain a variety of priority vitamins and minerals (12–14). The present goal was to assess nutrient density, affordability and carbon footprint of pulses as compared to other protein foods, both animal and plant as listed in the food composition tables (15).
The present sustainability analyses relied on databases developed and maintained by the US Department of Agriculture (USDA) and by other federal agencies (15, 16). Pulses were compared to other protein foods, both animal and plant, across three dimensions of sustainability: nutrient content, price, and environmental impact, the latter assessed using greenhouse gas emissions (GHGE) and cumulative energy demand. Nutrient density of pulses and other protein food sources was assessed using the Nutrient Rich Food (NRF9.3) index, a well-established method to assess nutrient density and the healthfulness of foods (17–19). Affordability metrics used national food prices recently released by the USDA (20). Data on greenhouse gas emissions (GHGE) and energy demand came from dataFIELD (21) and other published LCA data (22, 23).
2 Methods
2.1 Nutrient content, food prices, and environmental impact databases
The nationally representative National Health and Nutrition Examination Survey (NHANES) has a dietary component known as the What We Eat in America (WWEIA) study. The present analyses used the 2017–18 cycle (NHANES 2017–18). Energy content and nutrient composition of foods reported as consumed by NHANES participants came from the USDA Food and Nutrient Database for Dietary Studies (FNDDS 2017–18) (24). Individual food items in the FNDDS 2017–18 (identified by 8-digit codes) are aggregated by the USDA into food groups, food categories, and food subcategories using WWEIA 1-digit, 2-digit, and 4-digit codes (25).
Included in the USDA WWEIA protein foods group are the categories of red meat (beef, pork, lamb, and game), poultry, seafood, eggs, beans and legumes, and nuts and seeds. The beans and legumes category can be disaggregated into subcategories of pulses and soy products, the latter being mostly processed soy. The pulses subcategory includes beans, peas, chickpeas, lentils, and beans with meat. Beans with meat were evaluated separately. Milk and dairy products fall outside the protein food group, even though they contribute high quality protein to the US diet.
Mean national retail prices for 3,231 food codes in the FNDDS 2017–18 database came from recently released USDA data files (26). The USDA Purchase to Plate Price Tool (PPPT) (20) collects scanner data from retailers and converts retail prices (US$ per product) to unit prices (US$ per 100 g edible portion), adjusting for consumer-level losses and waste. Prices were available for approximately 50% of FNNDS foods that represented 97% of total intake by weight (20).
Data on GHGE and energy demand came from the database on Food Impacts on the Environment for Linking to Diets (dataFIELD), which was developed using a systematic review of LCA studies published between 2005 and 2016 (21). The GHGE and energy demand estimates were averaged across studies and were matched to commodities in the 2010 US Environmental Protection Agency (US EPA) Food Commodity Intake Database (FCID) (16). The FCID provides information on the amount of >500 food components in each food reported as consumed by NHANES participants. The FCID data had been matched with the FNDDS 2017–2018 (23). These data had been used in other studies on the environmental sustainability of alternative dietary patterns in the US (22). The databases were merged using WWEIA 8-digit food identification codes.
2.2 Derived variables
2.2.1 Nutrient rich foods index
The Nutrient Rich Food Index (NRF), developed in 2009 (17) is a compensatory nutrient profiling (NP) model that is composed of a positive Nutrient Rich (NRn) sub score and a negative nutrients to limit (LIM) sub score. The positive NRn sub score is based on a variable number n of nutrients to encourage, generally protein, fiber, and a variety of vitamins and minerals. The negative LIM sub score is generally based on the same 3 nutrients to limit: saturated fat, total or added sugar and sodium (17–19). Percent daily values per reference amount are calculated using nutrient standards from the Food and Drug Administration values for a 2,000 kcal/day diet (27). The FDA nutrient standards are shown in Table 1.
Table 1. Reference daily values (RDV) for nutrients to encourage and nutrients to limit based on a 2,000 kcal diet.
Dietary reference intakes for potassium were set at 3,500 mg and did not follow the FDA standards. The FDA sets the DV for potassium at 4,700 mg/day; however, based on survey studies, less than 3% of the population consumes that amount (28). In 2019, the National Academies updated the Dietary Reference intakes for potassium that now stand at 3,400 mg for men and 2,600 mg/d for women (29, 30). The current opinion is that potassium between 3,500 and 4,700 mg/day has benefits for lowering blood pressure (28). The European Food Safety Authority (EFSA) recommends at least 3,500 mg/day of potassium (31). Whereas nutrient density calculations conducted in the US tend to use FDA standards, calculation conducted in other countries, especially lower income countries, tend to use standards from Codex Alimentarius or the Food and Agriculture Organization of the United Nations.
The commonly used NRF9.3 version of the NRF family of scores is composed of a NR9 sub score that is based on %DV for 9 nutrients to encourage: protein, fiber, calcium, iron, potassium, magnesium, vitamin A, vitamin C, and vitamin D. Those nutrient choices were guided by the FDA requirement that the use of term healthy on food labeling only applied to foods that provided at least 10% of DV for protein, fiber, calcium, iron, vitamin A and vitamin C (32). The current FDA Nutrition Facts Panel also lists %DV for potassium and vitamin D. Dietary surveys of the US population show that many people consume less than recommended amounts of magnesium (33).
Typically, nutrient content is expressed as percent daily value (%DV) per 100 kcal but can also be expressed per 100 g of food (34). The NR9 sub score is the sum of %DV, with each %DV capped at 100%.
The negative LIM sub score is always composed of Maximum Recommended Values (MRVs) for the same 3 nutrients to limit: saturated fat, total or added sugar, and sodium. The existing FDA regulations for the nutrient content claim “healthy” disqualify foods with excess amounts of saturated fat and sodium. Limiting added sugar is a global health policy. Percent MRV for nutrients to limit can be calculated per 100 kcal or per 100 g. The LIM sub score is the sum of %DV, with each %DV capped at 100%.
The final NRF9.3 score is given as the sum of %DV for nutrients to encourage minus the sum of %MRV for the 3 nutrients to limit. Thus NRF9.3 = NR9-LIM. The NRF score has been validated multiple times with respect to independent measures of a healthy diet.
2.2.2 Affordable nutrient density index
Nutrient profiling systems, such as the Nutrient Rich Foods Index, provide information that can be used to compare the nutrient content of foods, but they do not measure affordability. This is an important metric to capture because affordable nutrient density represents one way to evaluate access to sustainable healthy diets (35). Therefore, we used the Affordable Nutrient Density Index to assess energy content and nutritional value of foods in relation to their cost (36). To be nutrition-relevant, such economic indicators are normally expressed in terms of monetary cost per calorie or per nutrient, as opposed to food weight (35). Food prices data are typically collected and expressed per 100 g of food, edible portion. The present analyses converted food prices to prices per 100 kcal of food. The Affordable Nutrient Density index is a simple ratio of nutrient density per 100 kcal to food prices, also calculated per 100 kcal. Such methods help to identify those foods in the protein foods group that provide most nutrient density per penny (36, 37). An alternative way to calculate protein cost is to estimate the monetary cost of providing a given amount of protein from a given food (38), for example 50 g which is equal to 100% of the daily value.
2.2.3 Environmental cost of pulses
Environmental metrics are typically converted to common units to account for differences in measurement. GHGE are expressed as kg CO2 equivalents because different greenhouse gases have very different global warming potential. For example, the global warming potential of nitrous oxide (N2O) and methane (CH4) is up to 265 and 28 times greater than carbon dioxide (CO2), respectively, over a 100-year timescale. Energy demand represents the amount of non-renewable energy used throughout the life cycle of a given food, which includes agricultural production, processing, supply chain, and home preparation. At each stage, different forms of energy are used (electricity, natural gas, gasoline, etc.) that embody very different amounts of energy, so these are converted to MJ.
GHGE values (kg CO2 equivalents) and energy demand (MJ) are typically expressed relative to their food weight (i.e., per 100 g). The present calculations of GHGE and energy use focused on the environmental cost associated with providing 50 g of protein, equivalent to 100% of the daily value. For purposes of the present analyses, protein was not corrected for digestibility using the Protein Digestibility Corrected Amino Acid Score (PDCAAS) (39) or the Digestible Indispensable Amino Acid Score (DIAAS) (40).
2.3 Plan of analysis
Analyses of nutrient density, affordability, and environmental impact used one-way ANOVAs by WWEIA food subcategory.
3 Results
3.1 The USDA protein foods group has the highest monetary and environmental cost
The USDA major food groups (identified by WWEIA 1-digit codes) are protein foods, milk and dairy, grains, vegetables, fruits, mixed dishes, snacks and sweets, fats and oils, condiments, and sugars. Figure 1 shows mean national food prices (in $/100 g of food) plotted against the mean carbon footprint (in kg CO2-eq/100 g of food) by food group. The size of the bubble reflects the mean protein content of the food group in g/100 g. The USDA protein food group had the highest protein content (>20 g/100 g) and also the highest monetary cost and GHGE. Consistent with past reports, national retail prices per 100 g were highest for the USDA Protein Foods Group (41) and so were greenhouse gas emissions (42). However, those figures generally apply to animal source proteins (42). Subsequent analyses focused on the Protein Foods Group only, and separated animal proteins from plant proteins.
Figure 1. Mean monetary cost ($/100 g) plotted against greenhouse gas emissions (Kg CO2eq/100 g) by USDA food group in the FNDDS 2017–18 database. Size of bubble reflects mean protein content in g/100 g for each food group.
3.2 Protein food categories and subcategories
The protein foods group was then disaggregated into categories and subcategories, based on WWEIA codes (25). First, the red meat category was separated into beef, pork, lamb, and cured meats. There was a separate category of organ meats (liver). Poultry was separated into chicken and turkey (43). Plant proteins were separated into beans and legumes, and nuts and seeds. The beans and legumes subcategory was then separated into pulses, pulses with meat, and soy products (mostly processed soy).
Figure 2 shows protein content in g/100 g of food, by food category, plotted against prices ($/100 g). The size of the bubble reflects the relative mean nutrient density of each food category, as indexed by the NRF9.3 score. Most meats and fish had a mean protein content of >20 g per 100 g. Foods that were highest in protein were pork, turkey, beef, and lamb. Pork items contained a mean of 25.4 g of protein per 100 g, as compared to 27.3 g/100 g for beef and 23.2 g/100 g for chicken (43). Pulses on average provided under 10 g of protein per 100 g.
Figure 2. Protein content (g/100 g) plotted against monetary cost ($/100 g) by USDA protein foods subcategory with nutritional profiling. The size of bubble reflects the Nutrient Rich Food Index NRF9.3 value.
On the other hand, pulses were the lowest cost protein source, with mean prices well below all animal proteins, other than eggs. The highest food prices per 100 g were for shellfish, lamb, fish, and beef. Consistent with the Thrifty Food Plan 2021 report (41), shellfish were much more costly compared to other protein foods. Per 100 g of food, mean national prices for pork were below beef and fish and closer to chicken and turkey (41).
Consistent with past observations, the highest NRF9.3 nutrient density scores (i.e., larger circles represent higher NRF9.3 scores) were observed for liver, fish, pulses, shellfish, and soy products. The lowest values were obtained for cured meats.
3.3 Protein content of foods in relation to GHGE and energy demand
Figure 3A shows mean food prices ($/100 g) again plotted by mean protein content (g/100 g) by food category, but the size of the bubble is now proportional to the estimated mean GHGE values by category. The highest GHGE values were for beef, lamb, shellfish, liver, and cured meats. Figure 3B also shows mean food prices ($/100 g) plotted against mean protein content (g/100 g) by food category but the size of the bubble is now proportional to the energy demand per 100 g. The highest energy demand was for shellfish and fish followed by cured meats. Compared to meats and fish, pulses had lower protein content. However, in every case, pulses benefited from the lowest prices and the lowest environmental cost.
Figure 3. Protein content (g/100 g) plotted against monetary cost ($/100 g) by USDA protein foods subcategory with environmental impacts. (A) The size of bubble reflects greenhouse gas emissions (Kg CO2eq/100 g) GHGE; (B) The size of the bubble reflects energy demand per 100 g.
Mean national food prices and environmental cost by protein food subcategory are also shown in Table 2. Pulses had the lowest monetary cost, GHGE values, and energy demand (all calculated per 100 g).
Table 2. Protein food group subcategories and their monetary, greenhouse gas emissions in kg CO2 eq per 100 g (GHGE) and energy demand values.
3.4 Affordable nutrient density index
Subsequent calculations focused on nutrient density per unit cost. The affordability index is generally calculated by dividing nutrient density scores calculated per 100 kcal by food prices, also calculated per 100 kcal (36). The metric of affordable nutrient density is shown in Figure 4. Here we divide nutrient density NRF9.3 scores per 100 kcal by food price also per 100 kcal. Consistent with previous reports on the global cost pf priority micronutrients (44, 45), the most affordable nutrient rich foods were pulses (peas, beans, lentils, and chickpeas), organ meats (liver) and nuts.
Figure 4. Affordable nutrient rich food index (NRF9.3) values for protein foods by subcategory.
3.5 The monetary and environmental cost of 50 g (100% DV) protein
Table 3 shows the monetary and environmental cost per 50 g of protein by category. Pork meat provided 100% DV of protein for a price that was closer to chicken and eggs than it was to lamb or beef (43). This was the result of the high protein content of pork meat and relatively low price as compared to non-poultry meats (43). Other low-cost protein sources were chicken, eggs, turkey, and pulses. Shellfish were the most expensive protein source, whether per 100 g or per 50 g of protein. The high price of shellfish was also noted in the TFP 2021 report (41).
Table 3. Protein food group subcategories and their monetary, greenhouse gas emissions in kg CO2 eq per 100 g (GHGE) and energy demand values.
Pulses had the lowest environmental footprint per 50 g protein when measured in terms of GHGE. Pulses were followed by turkey, soy, and fish. Pulses also had the lowest environmental footprint per 50 g protein when measured in terms of energy demand per 50 g protein. It needs to be mentioned that the present data were not corrected for PDCAAS (Protein Digestibility Corrected Amino Acid Score). Based on still limited PDCAAS data, meats have more digestible protein per 100 g than plant-based proteins, except for soy (39).
4 Discussion
The four dimensions of sustainability are nutrition and health, economics, environment and society. Each domain has its own indicators and metrics. To conduct sustainability research, it is necessary to merge siloed data, often maintained by different agencies, to arrive at metrics of nutrient density, affordability, and environmental impact of foods. The lack of data interoperability can be a challenge (46).
The present analyses dealt with three out of four sustainability domains, relying on food composition data and mean national food prices generated by the USDA, as well as life cycle analyses from published studies. The present analyses show that pulses had low cost and low carbon footprint compared to other protein foods and provided low-cost protein (after pork) and the most affordable nutrient density per penny. The present results can be linked to some ongoing food and nutrition policy initiatives in the US and elsewhere.
First, the current edition of DGA 2020–25 recommends that the Healthy U.S.-Style or Healthy Mediterranean-Style dietary pattern ought to include 1.5 cups of pulses per week for adults consuming 2,000 kcal/d (47). The Healthy Vegetarian diet pattern requires another 6 cups per week for a total of 7.5 (47). For comparison, the most recent NHANES data show that adults consume an average 0.12 cups of legumes per day (which includes pulses and soybeans). US adults have a long way to go to meet the recommended intakes for pulses.
As the present analyses show, pulses score high on nutrient density metrics. Among food categories, pulses are unique in providing approximately equal amounts of protein and fiber and are rich in potassium and folate (48). The selection of index nutrients for the present NRF9.3 nutrient profiling model was guided by current federal regulations and Dietary Guidelines for Americans. One advantage of the NRF approach is that is adaptable and can incorporate new nutrients and/or dietary ingredients as new data become available (34).
Modeling studies suggest that replacing protein foods with pulses leads to more nutrient rich and higher quality diets. In one study, a mix of protein foods (meat, chicken, fish, eggs, nuts, seeds, and soy) with the pulses composite in the 2,000 kcal/day US Style Healthy Food Pattern. The substitution od 6–8 oz/week of protein foods with 1.5–2.0 cups of pulses per week increased fiber and decreased cholesterol (49). Higher amounts of pulses generally led to diets with more fiber, iron, magnesium, potassium and copper depending on the type of substitution modeling (49). Another study (50) found that partial replacement of red and processed meats with plant proteins could be done while maintaining sufficient protein and amino acid profiles. The amount of pulses that would provide sufficient nutrients to qualify for nutrient content claims under regional regulatory frameworks was estimated at 100 g or 125 ml (0.5 metric cup) (12).
Second, protein is indeed the costliest nutrient – in terms of both price and environmental cost. However, the USDA protein foods group needs to be disaggregated into animal and plant proteins and those need to be separated into categories. For example, pork has been traditionally put together with red meat in studies on diet quality and health. Once pork was treated as a separate category, it was shown to be distinct in terms of price and environmental cost (43, 51). The present data confirm that pork meat was closer in price to chicken and turkey than to beef and lamb. Meanwhile, pulses can provide consumers with a more sustainable protein option with a high nutritional value per cost (52, 53). That finding may have implications for the redesign of the USDA Thrifty Food Plan, the modeled healthy diet at an affordable cost.
Third, GHGE values and energy demand are typically calculated per weight or volume of food. Arguably, kilogram is not an appropriate measure of nutritional value. There have been attempts to express GHGE values per 1,000 kcal or per 1 kg of protein (54). At least one study suggested that protein ought to be a nutritional functional unit (NFU) in lifecycle analyses (55). An FAO report suggested that a NFU could be based on nutrient density metrics, for example the Nutrient Rich Food Index (NRF) (56).
Fourth, there is explanatory value in disaggregating food groups into their constituent food categories and individual foods. Pulses were further separated into peas, beans, chickpeas, and lentils. The Affordable NRF9.3 gave highest scores to peas, beans, and lentils. These were followed by chickpeas, nuts and beans with meat. When it comes to environmental impact, pulses had the lowest GHGE per 50 g protein – below nuts, fish, soy, and turkey. Calculations of environmental cost of protein were very favorable for pulses.
Finally, there are tradeoffs to be made. Pulses are in the protein group, but their protein content per 100 g is below that of meat and fish (<10 g as opposed to >20 g/100 g). Pulses have a lower protein content than do nuts and soy products (7 g/100 g as opposed to 17 g/100 g for nuts). But pulses compensate for that in that the price per 50 g protein is much lower; effectively pulses offer the most protein (and other key nutrients) per penny.
There are cautions and limitations. The present analyses used combined publicly available USDA and other federal agency databases to evaluate multiple domains of sustainability, consistent with the foundational FAO framework (56) and with past research (57, 58). However, there were data gaps and prices and environmental impact data were not available for all foods in the FNDDS 2017–18 database. For example, the prices do not reflect recent inflation. The Purchase to Plate Price Tools (PPPT) used in this study was derived by linking retail grocery scanner data with the USDA Food and Nutrient Database for Dietary Studies (FNDDS). The USDA-generated PPPT allows users to link data on food intake with price estimates per 100 g edible portion. In 2023 the USDA made Purchase to Price National Average Prices (PP-NAP) available for NHANES cycles 2011–2018. Data for 2019–20 are expected no earlier than fall 2025. Data for 2023–4 are not available at this time. Given the complexities of food inflation, we have made no independent attempt to adjust to post-COVID 2023 or 2024 prices.
Similarly, data on environmental impact of foods were limited to greenhouse gas emissions and energy demand. Energy demand refers to the estimates of energy required for food production (23) Those published data have been derived from multiple sources, both in Europe and the US (59). One problem with the available data on energy, land and water use is that they are rarely context specific. The environmental cost of food products varies by climate and geographic location, For example, pooled data for the classic paper by Poore and Nemecek (54) came from 38,000 farms in 119 countries.
Given the lack of PDCAAS values for FNDDS foods, the data could not be corrected for r protein digestibility. PDCAAS values for pulses are in the order of 0.80 rather than 1.00 (39). This is an important caution and this issue will need to be addressed in future calculations. In practice, pulses have been combined with other foods to meet indispensable amino acid requirements. Future analyses may need to take combinations of foods into account. Further, pulses contain phytates that interfere with iron absorption (60–62). Phytate content can be reduced by soaking and cooking (61).
The present analyses were based on in foods consumed by NHANES participants that included a variety of pulses and pulse dishes. It is important to note that pulses are also used in the manufacture of alternative plant proteins developed from, e.g., pea protein isolates. The present analyses did not examine protein concentrates and isolates that are used to manufacturers plant-based alternatives to milk and meat. Replacing animal protein in the diet may take the form of more plant foods or more alternative proteins (63).
Indicators of the social value of pulses globally were not examined. Pulses are a key component of the Mediterranean diet (64) and are widely recommended (65) and accepted in many cultures as culinary ingredients (66). The Food and Agriculture Organization of the United Nations lists 11 types of pulses, namely dry beans, dry broad beans, dry peas, chickpeas, cow peas, pigeon peas, lentils, Bambara beans, vetches, lupins, and other pulses Future studies will examine trends in pulses consumption in the context of rising incomes and the global nutrition transition.
5 Conclusion
A shift toward more environmentally sustainable diet patterns should not compromise diet quality or affordability. By combining multiple publicly available databases on food nutrient content, prices, and environmental impacts, and leveraging several nutrient profiling systems, we show that pulses stand out among plant protein foods. Pulses, which include beans, peas, lentils, and chickpeas, were the lowest cost source of protein and other nutrients and had the lowest environmental impacts.
Data availability statement
Publicly available datasets were analyzed in this study. This data can be found at: https://www.ars.usda.gov/ARSUserFiles/80400530/pdf/fndds/FNDDS_2017_2018_factsheet.pdf (Accessed 14 May, 2024), https://www.ers.usda.gov/data-products/purchase-to-plate/ (Accessed May 14, 2024), and from the following publications: doi:10.1016/j.ajcnut.2023.04.018; doi: 10.3389/fnut.2022.868485; and doi: 10.1186/s12937-020-00629-6.
Author contributions
AD: Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Visualization, Writing – original draft, Writing – review & editing. ZC: Conceptualization, Data curation, Funding acquisition, Investigation, Methodology, Project administration, Writing – review & editing.
Funding
The author(s) declare that financial support was received for the research, authorship, and/or publication of this article. Financial support was received from the USDA ARS FY 2023 Pulse Crop Health Initiative (58-3060-3-050).
Acknowledgments
The authors thank Kayla Hooker for editorial work.
Conflict of interest
AD is the original developer of the Naturally Nutrient Rich (NNR) and the Nutrient Rich Food (NRF) nutrient profiling models and is or has been a member of scientific advisory panels for BEL, Lesaffre, Nestlé, FrieslandCampina, National Pork Board, and Carbohydrate Quality Panel supported by Potatoes USA. AD has worked with Ajinomoto, Ayanabio, FoodMinds, KraftHeinz, Meiji, MS-Nutrition, Nutrition Impact LLC, Nutrition Institute, PepsiCo, Samsung, and Soremantec on quantitative ways to assess nutrient density of foods. ZC has research awards from the National Pork Board and the Jeffress Trust Awards Program in Research Advancing Health Equity, serves on a Technical Working Group for the US Department of Agriculture’s Food and Nutrition Service, and receives research consulting fees from Johns Hopkins University.
The author(s) declared that they were an editorial board member of Frontiers, at the time of submission. This had no impact on the peer review process and the final decision.
Publisher’s note
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Keywords: pulses, protein, national food prices, affordability, greenhouse gas emissions, sustainability, nutrient rich food index
Citation: Drewnowski A and Conrad Z (2024) Pulse crops: nutrient density, affordability, and environmental impact. Front. Nutr. 11:1438369. doi: 10.3389/fnut.2024.1438369
Edited by:
Aaron Christian, University of Ghana, GhanaReviewed by:
Henry J. Thompson, Colorado State University, United StatesChristopher P. F. Marinangeli, Protein Industries Canada, Canada
Copyright © 2024 Drewnowski and Conrad. 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: Adam Drewnowski, YWRhbWRyZXdAdXcuZWR1