Volume 7, Issue 1 (March 2022)                   J Environ Health Sustain Dev 2022, 7(1): 1583-1593 | Back to browse issues page


XML Print


Download citation:
BibTeX | RIS | EndNote | Medlars | ProCite | Reference Manager | RefWorks
Send citation to:

Noormohammadi M, Eini-Zinab H, Rezazadeh A, Omidvar N, Sobhani S R. A Step toward a Sustainable Diet by Reducing Carbon Footprint: A Case Study in Iran. J Environ Health Sustain Dev 2022; 7 (1) :1583-1593
URL: http://jehsd.ssu.ac.ir/article-1-369-en.html
Department of Nutrition, Faculty of Medicine, Mashhad University of Medical Sciences, Mashhad, Iran.
Full-Text [PDF 873 kb]   (346 Downloads)     |   Abstract (HTML)  (1231 Views)
Full-Text:   (414 Views)
A Step toward a Sustainable Diet by Reducing Carbon Footprint: A Case Study in Iran

Morvarid Noormohammadi 1, Hassan Eini-Zinab 2, Arezoo Rezazadeh 2, Nasrin Omidvar 2, Seyyed Reza Sobhani 3*

1 Student Research Committee, Department of Community Nutrition, Faculty of Nutrition and Food Technology, National Nutrition and Food Technology Research Institute, Shahid Beheshti University of Medical Sciences, Tehran, Iran.
2 Department of Community Nutrition, Faculty of Nutrition and Food Technology, National Nutrition and Food Technology Research Institute, Shahid Beheshti University of Medical Sciences, Tehran, Iran.
3 Department of Nutrition, Faculty of Medicine, Mashhad University of Medical Sciences, Mashhad, Iran.
A R T I C L E  I N F O ABSTRACT
ORIGINAL ARTICLE Introduction: Greenhouse gas (GHG) emissions have caused environmental effects. Food production is one of the sources of GHGs. This study aimed to suggest dietary scenarios for decreasing GHG emissions.
Materials and Methods: GHG emissions in the target population of Urmia city, Northwest Iran, were investigated using a modeling approach. Three dietary scenarios were modeled and analyzed to evaluate and compare GHG emissions. The objectives and decision variables of the three scenarios included minimizing the carbon footprint and intake of food items, respectively. In the first scenario, the amount of energy intake was equal to baseline energy intake. The second scenario maintained the same energy intake constraint as the first scenario and made further alterations by considering the number of serving sizes suggested by the food pyramid for each food group. The third scenario was mostly based on this model by accounting for dietary reference intake for macronutrients, micronutrients, and energy.
Results: There was about 72% and 55.67% reduction in carbon dioxide equivalent (CO2 eq) production in the first and second scenarios rather than the baseline diet of 4072.10 g CO2 eq, respectively. In the final scenario, the CO2 eq emissions were less than half of the baseline diet.
Conclusion: The study showed that a healthy diet with a higher proportion of vegetables, fruit, legumes, nuts, and dairy, and a lower share of red and white meat, egg, grains, fat and oil, and sweets can reduce CO2 eq emissions.

Article History:
Received: 26 October 2021
Accepted: 20 January 2022

*Corresponding Author:
Seyyed Reza Sobhani
Email:
Seyyedrezasobhani@gmail.com
Tel:
+985138002422

Keywords:
Greenhouse Gases,
Diet,
Carbon Footprint,
Diet, Vegetarian,
Environment.
Citation: Noormohammadi M, Eini-Zinab H, Rezazadeh A, et al. A Step toward a Sustainable Diet by Reducing Carbon Footprint: A Case Study in Iran. J Environ Health Sustain Dev. 2022; 7(1): 1583-93.
Introduction
Climate change is a threat to food security. Climate variability and related challenges have led to global hunger by affecting agricultural production in recent years 1. The global increase in greenhouse gas (GHG) emissions is a significant concern that needs to be addressed. Many countries have programmed to reduce their emissions 2. On the other hand, food production is the most considerable artificial pressure on the planet that threatens the local ecosystems and Earth system stability 3. The global food system is responsible for about 35% of the GHG emissions in the world 4. In recent years, there has been a trend in consuming more processed foods, and producers compete to use land, water, and energy, negatively affecting environmental sustainability 5. It is estimated that in 2005, total emissions from cattle production were about 4623 million tonnes CO2 eq 6. The current food system is responsible for food and nutrition insecurity and is one of the most significant contributors to damaging the planet in all production, storage, and processing steps to consumption 7. Therefore, it is required to create a global change in the food system to obtain sustainable diets 1, 3.
Sustainable diets have low environmental impacts, contributing to food and nutrition security and healthy life for present and future generations. Determining a dietary scenario with low GHG emissions is a step toward a sustainable diet 8, 9. The idea of sustainable diets combines the difficulties inherent in developing a food system capable of providing nutritious foods to a growing population while minimizing environmental damage and remaining within planetary limits. In the last decade, research on sustainable diets has significantly developed 10. According to the EAT-Lancet report, by 2050, it is necessary and achievable to follow sustainable dietary patterns with adequate caloric intake, including a variety of plant-based foods, unsaturated rather than saturated fats, and low amounts of refined grains, added sugars, animal-based and highly processed foods 3.
To the best of the authors’ knowledge, no study has been conducted in Iran to design sustainable and environmentally-friendly dietary scenarios through reducing carbon footprint and considering health benefits. Therefore, this study aimed to suggest dietary scenarios to decrease GHG emissions by considering nutritional recommendations and the food preferences of individuals.

Materials and Methods
Study design and sampling
This modeling study was performed as part of a larger project entitled ‘Designing and testing a multilevel model to explain the effects of the neighborhood, household, and individual levels on anthropometric factors in men and women living in the city of Urmia' 11-13. The sample size of the main study was 723 (427 women and 296 men), aged 20-64 years in two ethnic groups (445 (61·5%) Azeri Turks and 278 (38·5%) Kurds). The procedures for sample selection and data collection are presented elsewhere 11. Samples selection was conducted using a combination of the cluster, random, and systematic sampling methods. The selection was made from all four geographical zones (north, south, east, and west) of Urmia. Health centers were clusters that were randomly selected according to population size at each geographical zone. Then households were selected. In each center, the first household of each cluster was selected from the routine data registry of the center. The interview was done with household members (one man and one woman) by trained local nutritionists who were fluent in Turkish and Kurdish. Using the cluster sampling method, an attempt was made to minimize sampling error in the sampling stage.
Data collection
Dietary data were collected by a 168-item semi-quantitative food frequency questionnaire. The questionnaire utilizes a Willett format and was modified based on Iranian food items and was used to collect information on food intake over the past year 14. The questionnaire contained a list of food items commonly consumed by Iranian people, with standard consumables. The participants in the study were asked to report the consumption frequency of each food item over the year prior to the study on a daily, weekly, monthly, or annual basis. The validity and reliability of this questionnaire have been reported and approved for the Iranian population 15. However, to apply it in Urmia city, which is ethnically diverse, the content validity of the questionnaire was evaluated by five local nutritionists in the nutrition department of Urmia University of Medical Sciences 13. In addition, to minimize the response error, individuals who reported energy intake over ± 3 standard deviations (SD) from the mean energy intake were excluded from the study.

Statistical analysis
After data collection, the consumption frequency of each food item was converted to each individual’s daily intake over the previous year, and portion sizes were converted to grams by using household consumption units 16. Then the mean intake of different food items in the study population was used to continue the calculations. An adapted version of NUTRITIONIST 4 software that allows the user to do nutritional analysis on single food items, recipes, meals, and entire diets and contains Iranian food composition table (version 7.0; N-Squared Computing, Salem, OR, USA) was used in this study. This software determined the amount of nutrients and energy in the mean intake of different food items of individuals, based on the amount of nutrients and energy in each food item. Those who failed to complete a minimum of 50% of the questionnaire items or their energy intakes were classified as incorrect reports according to the Goldberg method and were excluded from study 17.
The ‘carbon footprint' method was adopted to calculate CO2 eq emissions during food production. The carbon footprint is a measure that shows how many kilograms of carbon dioxide eq is produced per kilogram of food, directly and indirectly, caused by an activity or is accumulated over the life stages of that product 18. Since there is no data in this regard in Iran, the CO2 eq emissions of each food item were taken from “BCFN Double Pyramid Database”. Food Climate List was used from the Swedish University of Agricultural Sciences for some food items that were not available in the BCFN data, such as candy, ice cream, tea, ketchup, imported fruit, oil, jams, legumes, and nuts. These data report kilograms of carbon dioxide eq produced per kilogram of food. Then, using this data and based on the mean food intake calculated, a simple proportion was used to calculate CO2 eq for each food item 19.
Linear programming (LP) technique in the MS Excel (version 2013) Solver add-on was employed to model optimal food pattern while considering carbon footprint 20. LP for designing diets has been described in detail elsewhere 21. In this study, the LP-designed models were low- CO2 eq based diets. The main elements of LP models include the objective, decision variables, and constraints. The objective sets the optimal goal. In the present study, the goal was to minimize the carbon footprint. Changing variables are those decision variables that can be varied to reach the objective by considering constraints. The decision variables in this study were the amounts of food items. The constraints are those conditions that must be fulfilled to reach the objective goal. LP investigated three scenarios to identify a healthy plate with a low carbon footprint for the Urmia population. These three scenarios aimed to investigate the effect of a step-by-step move from a regular diet to a healthy diet on carbon footprint. The objectives and decision variables for all three scenarios were minimizing the carbon footprint and intake of food items, respectively. To consider the population's dietary habits, in all scenarios, the first and third quartiles of the baseline food intake were considered the minimum and maximum amount of each food item. “Baseline diet” refers to the average observed diet in the study population.
In some cases where the third quartile cut point was less than a serving size, the latter was the maximum. Additional constraints for each scenario were set as follows. In the first scenario, the amount of energy intake of the model was equal to the baseline energy intake, which is the mean energy intake in the population. In the second scenario, in addition to the energy constraint of the earlier scenario, the number of serving sizes suggested by the food pyramid for each food group was considered a constraint. The recommended amounts of cereals, vegetables, fruit, dairies, meat, legumes, and egg in food-based dietary guidelines for Iran are 6-11 (minimum-maximum), 3-5, 2-4, 2-3, and 2-3 servings, respectively 22. In the third scenario, in addition to all the constraints that were considered in the second scenario, the recommended dietary allowance (RDA) for macronutrients, micronutrients, and energy were considered constraints. An RDA is the average daily dietary intake level that is enough to meet the nutritional needs of 97 to 98 percent of healthy people in the community 23. Since the studied population included male and female adults, based on their share in the sample size, the weighted average of WHO and FAO recommended for macronutrients, micronutrients, and energy were used 24-26. These three scenarios were compared with "baseline diet" based on the contribution of each food group on total energy for each scenario, macro and micronutrient composition, and the amount of carbon footprint.

Ethical Issue
All procedures were conducted according to the latest version of the Helsinki Declaration. The study was approved by the ethics committee of “Student Research Committee” “Research Technology Chancellor” in Shahid Beheshti University of Medical Sciences, Tehran, Iran (IR.SBMU.RETECH.REC.1396.495).

Results
Data were analyzed for 695 participants. Due to the misreporting of energy intake and incomplete food frequency questionnaire (more than 50 % of items blank), 28 (4.9%) individuals were excluded. The results were ordered by model-generated diets of different scenarios and checked against baseline intake or RDA. The share of total energy intake supplied by each food group in the baseline model, and three scenarios are presented in Figure 1.
Regarding diverse sub-groups of the “meat, poultry, fish, dry legumes, egg, and nuts” group, the contribution of each sub-group in the baseline intake and three scenarios are presented in Table 1. Macro and micronutrient content of baseline intake and each scenario were compared with RDA (Table 2).
In the baseline model, the “bread, cereal, rice, and pasta” group (i.e., 39%) had the highest proportion of average energy intake 2920 Kcal. The lowest contribution belonged to "fruit" and "vegetables" (i.e., 8% contribution of each group). The amounts of macronutrients, micronutrients, and energy in the baseline diet were higher than RDA. The CO2 eq emission of baseline intake was 4072.10 g for the daily food of a person.
In the first scenario, the LP goal was to minimize the carbon footprint while taking the same amount of daily energy without considering nutritional requirements. In this model, the share of "meat, poultry, fish, dry legumes, egg, and nuts" and "vegetables" in supplying daily energy increased by 168% and 200%, respectively, compared to the data from the baseline diet. On the other hand, the contribution of “milk, yogurt, and cheese” (93%), “bread, cereal, rice, and pasta” (56%), “fruit” (25%), and “fat, oil, and sweets” (16%), decreased.
The total contribution of red meat, fish and poultry, legumes, and egg decreased 95%, 69%, 26%, and 70%, respectively, and the share of nuts has  increased about 16 times, in the first scenario compared to the baseline intake. In terms of macro nutritional components, carbohydrate was 6% less than RDA. Also, sodium intake was 54% more than RDA, and vitamin A, calcium, riboflavin, vitamin B12, and vitamin K intakes were 80%, 32%, 9%, 68%, and 21% less than the recommended values for adults, respectively. By these modifications, CO2 eq emission was 1128.40 g and decreased by about 72.29% compared to the baseline intake.
  
Figure 1: The portion of total energy intake supplied by each food pyramid group according to baseline diet and modeled scenarios

Table 1: The contribution of each food subgroup in grams according to baseline diet and modeled scenarios
Subgroups Baseline diet Scenario 1 Scenario 2 Scenario 3
Meat, poultry, fish, dry  legume , egg, and nuts 202.54 229.72 106.54 104.8
Read meat 51.30 2.7 2.70 3.95
Fish and poultry 51.32 15.86 15.86 15.86
Legumes 52.29 38.73 44.15 56.08
Nuts 9.66 161.01 32.40 17.49
Egg 37.98 11.46 11.46 11.46
Bread, cereal, rice, and pasta 532.56 221.12 319.76 314.93
Vegetables 448.41 465.61 383.58 334.69
Fruit 449.03 184.79 299.84 294.76
Milk, yogurt, and cheese 452.29 39.64 547.42 433.95
Fat, oil, and sweets 100.39 65.89 63.89 63.89
All values are reported in grams.

Table 2: The amount of micronutrients, macronutrients, and energy content according to baseline diet and modeled scenarios compared to RDA
Baseline diet Scenario 1 Scenario 2 Scenario 3 RDA
Kcal 2920.17 2920.17 2920.17 2675.24 2675.24
Protein (g) 111.30 80.48 75.20 75.96 50.1
Carbohydrate (g) 426.11 344.08 380.51 367.84 367.84
Fat, total (g) 93.15 147.95 106.05 86.12 89.17
Sodium (mg) 3704.89 2309.32 2809.63 1500 1500
Vitamin A (RAE)(mg) 860.00 157.85 212.95 782 782
Vitamin C (mg) 187.30 84.15 86.45 88.12 81.15
Calcium (mg) 1450.84 681.29 1507.50 1017.07 1000
Ferrous (mg) 23.97 18.89 19.56 16.72 13.9
Thiamin (mg) 2.85 2.18 2.27 1.89 1.14
Riboflavin (mg) 2.88 1.08 2.67 1.99 1.18
Niacin (mg) 32.45 22.36 21.68 17.73 14.82
Vitamin B6 (mg) 2.36 2.66 1.70 2.28 1.3
Folate, total (mg) 701.04 621.72 596.40 420.24 400
Vitamin B12 (mg) 6.58 0.76 2.52 2.4 2.4
Vitamin k (mg) 250.36 80.94 82.21 102.3 102.3
Magnesium (mg) 476.23 550.26 394.75 388.27 346.9
Zinc (mg) 15.57 13.97 8.83 9.57 9.23
Fiber, total (g) 78.73 60.63 76.87 44.71 30.33
Cholesterol (mg) 366.41 89.79 128.03 249.68 300
Saturated fat (mg) 32.50 26.51 26.68 29.72 29.72
In the second scenario, a new constraint to the earlier model was added, which was to decrease the share of "bread, cereal, rice, and pasta" and "fat, oil, and sweets" by 37%, and 19%, respectively, compared to the baseline diet. Consequently, the contribution of “vegetables” (151%), “fruit” (3%), “milk, yogurt, and cheese” (35%), and “meat, poultry, fish, dry legumes, egg, and nuts” (2%) increased in providing the daily energy 2920 Kcal. However, there was a decrease in the contribution of red meat (95%), fish and poultry (69%), legumes and egg (16%), in this scenario, and the share of nuts increased to 235%, compared to the baseline intake. The amount of vitamin A (73%), vitamin K (20%), and Zn (4%) were less than the RDA, while sodium was (87%) higher than the recommended values. CO2 eq emission was 1805.1 g to supply a one-person diet for a day by following this scenario, which was 56% less than the baseline intake. Therefore, considering the food pyramid guidelines, the amount of CO2 eq emissions had a lower decline than the earlier scenario, where these references did not restrict the model.
In the third scenario, which was restricted to the food pyramid guidelines and RDA, the contribution of “bread, cereal, rice, and pasta”, “meat, poultry, fish, dry legumes, egg, and nuts”, and “fat, oil, and sweets” in providing average daily energy declined by 42%, 15%, and 12%, respectively, compared to the baseline diet. Also, the contribution of “vegetables” (20%), “fruit” (25%), and “milk, yogurt, and cheese” (115%) increased. The share of meat (92%), egg (70%), and also poultry and fish (69%), were less than the baseline intake. However, consumptions of legumes and nuts were, respectively, 7% and 81% more than the baseline intake. In this scenario, CO2 eq emission was 1928.09 g, which was 52% less than baseline intake.

Discussion
The present study suggested three different dietary scenarios for the target population to reduce CO2 production and provide a sustainable diet. The highest reduction in CO2 production (72%) compared to the baseline model was observed in the first scenario, which had an energy content equal to the baseline model but a larger amount of nuts within the meat group, followed by the second scenario (55.67% reduction in  CO2 production). In the third scenario that was completely in accordance with the food pyramid and RDA, the CO2 emission was less than half of the baseline model.
In the target population, per capita intake of rice and bread, oil, and sugar was 5%, 20%, and 38% more than the recommended values, respectively, while legumes, milk and dairy, egg and vegetables, and fruit consumption was lower than the recommended values. This type of food pattern is a challenge to food security in Iran 27. The majority portion of individual intake in the target community in Urmia was from bread and cereal (39%) and then fat (16%), and the least was for fruit and vegetables (8%).
Reducing the amount of dietary animal-based products was identified as a way to reduce carbon footprint 28. In the present study, the alternative scenarios with lower carbon footprints had a lower share of animal sources and a higher share of subgroups with plant sources. These alterations are consistent with previous research, indicating that meat production contributes 15%-24% of the total GHG emissions, primarily because of deforestation for grazing and having longer-lived animals required in meat production 29, 30. Similarly, removing meat from the UK diet resulted in a 35% decrease in GHG emissions 31. According to Springmann et al., substituting plant-based meals for animal-based foods is especially successful in high-income nations for mitigating certain environmental effects, most notably GHG emissions (reductions of up to 84%) 10. Soret et al. showed that moderate variations in meat product caloric consumption resulted in significant reductions in GHG emissions and better health outcomes, as shown by mortality studies 32.
By decreasing the meat group in this study, the contribution of legumes and nuts within this group increased. The amount of GHG emissions of ruminant meat (beef and lamb) per gram of protein is about 250 times more than legumes 33. Animal-based foods need more energy use than foods with a vegetable origin, so that they can affect the climate more seriously. The average fossil energy required for all animal protein production systems is more than 11 times that for grain protein production 34. Therefore, substituting legumes for meat may represent a healthy sustainable diet, but monitoring essential nutrients like zinc and iron is essential 35, 36.
Along with the shift in the proportion of the subgroup of meat, poultry, fish, egg, legumes, and nuts, the increased share of vegetable consumption also decreased CO2 emissions in contrast to baseline intake. Similarly, substituting fruit and vegetables for meat is illustrated to decrease diet-related GHG emissions in France 33. With a few minor deviations from what we observed, Chen et al. showed that a sustainable diet would involve a significant decrease in meat and vegetable oils consumption, a moderate drop in cereals, roots, and fish products consumption, and an increase in legumes, nuts, seeds, fruit, and vegetables consumption 37.
The dietary scenarios in this study also showed a reduction in fat, oil, and sweats. Vegetable oils have a lower carbon footprint and should be replaced with butter and hard margarine, and shortenings. Sweets and cakes probably have a high carbon footprint, although there is a lack of data on their contribution 38.
The present study is one of the few that deals with the relationship between diet and GHG emissions in Iran. A valid food frequency questionnaire was used. The cluster sampling method was used to minimize sampling error. However, a series of limitations should be considered in evaluating results. Although it was tried to exclude participants who reported their energy consumption more or less, when using a food frequency questionnaire to assess dietary intake, problems, such as under-reporting baseline intake or invalid reporting due to social desirability bias might have occurred 39.
Additionally, sustainable diets have different determinants like economic, environmental, culture, and health 40. This study considered only two dimensions, including the recommended
diet (health aspect) and CO2 emissions (environmental dimension). It would be better for future studies to consider other elements of a sustainable diet. In the present study, dietary habits of the population were considered in all scenarios as profiles of cultural and economic preferences of people. The suggested diet was limited to the first and third quartiles of the baseline food intake. However, suggested changes in the diet need to be more investigated from a feasibility aspect in future studies. Another problem was that there is not any carbon footprint data in Iran. Given that differences in the conditions of some countries, such as climatic conditions, can affect the carbon footprint of food items, the use of carbon footprint in other countries is not correct for Iran.


Conclusion
A healthy diet with a higher proportion of vegetables, fruit, legumes, nuts, and dairy group and lower consumption of meat, fish and poultry, egg, bread, cereal, rice, pasta, fat, oil, and sweets can supply all recommended dietary allowances while reducing CO2 eq emissions. However, the possibility and acceptability of varying amounts of the mentioned dietary groups must be established in a variety of geographical and sociocultural situations.

Abbreviations
FFQ: Food Frequency Questionnaire
RDA: Recommended Dietary Allowance
WHO: World Health Organization
LP: Linear Programming
FAO: Food and Agriculture Organization

Acknowledgments
This study is related to the project No. 1396/46469 from the Student Research Committee, Shahid Beheshti University of Medical Sciences, Tehran, Iran. The authors also appreciate the “Student Research Committee” and “Research & Technology Chancellor” in Shahid Beheshti University of Medical Sciences for their financial support of this study.

Funding
This work was supported by the Student Research Committee, Shahid Beheshti University of Medical Sciences, and Tehran, Iran.

Conflict of interest
The authors declare that there is no conflict of interest.

This is an Open-Access article distributed in accordance with the terms of the Creative Commons Attribution (CC BY 4.0) license, which permits others to distribute, remix, adapt, and build upon this work for commercial use.

References
  1. Macdiarmid J, Whybrow S. Nutrition from a climate change perspective. Proc Nutr Soc. 2019;78(3):380-7.
  2. Mokhtari M, Ebrahimi AA, Rezaeinia S. Prediction of greenhouse gas emissions in municipal solid waste landfills using LandGEM and IPCC methods in yazd, iran. J Environ Health Sustain Dev. 2020;5(4):1145-54.
  3. Willett W, Rockström J, Loken B, et al. Food in the Anthropocene: the EAT–Lancet Commission on healthy diets from sustainable food systems. Lancet. 2019;393(10170):447-92.
  4. Niles MT, Ahuja R, Barker T, et al. Climate change mitigation beyond agriculture: a review of food system opportunities and implications. Renew. Agric. Food Syst. 2018;33(3): 297-308.
  5. Godfray HCJ, Beddington JR, Crute IR, et al. Food security: the challenge of feeding 9 billion people. science. 2010;327(5967):812-8.
  6. Opio C, Gerber P, Mottet A, et al. Greenhouse gas emissions from ruminant supply chains–A global life cycle assessment: Food and agriculture organization of the United Nations; 2013.
  7. Food and Agriculture Organization Global food losses and food waste – extent, causes and prevention. 2011.
  8. Mekonnen MM, Hoekstra AY. A global assessment of the water footprint of farm animal products. Ecosystems. 2012;15(3):401-15.
  9. Pelletier N, Tyedmers P. Forecasting potential global environmental costs of livestock production 2000–2050. Proc Natl Acad Sci U S A. 2010;107(43):18371-4.
  10. Springmann M, Wiebe K, Mason-D'Croz D, et al. Health and nutritional aspects of sustainable diet strategies and their association with environmental impacts: a global modelling analysis with country-level detail. The Lancet Planetary Health. 2018;2(10):e451-e461.
  11. Rezazadeh A, Omidvar N, Eini-Zinab H, et al. Food insecurity, socio-economic factors and weight status in two Iranian ethnic groups. Ethn Health. 2016;21(3):233-50.
  12. Rezazadeh A, Omidvar N, Eini-Zinab H, et al. General and central obesity in two iranian ethnic groups living in Urmia, West Azerbaijan, Iran: effect of the neighborhood environment. Iran Red Crescent Med J. 2016;18(7).
  13. Rezazadeh A, Omidvar N, Eini-Zinab H, et al. Major dietary patterns in relation to demographic and socio-economic status and food insecurity in two Iranian ethnic groups living in Urmia, Iran. Public Health Nutr. 2016;19(18): 3337-48.
  14. Willett WC, Sampson L, Stampfer MJ, et al. Reproducibility and validity of a semiquantitative food frequency questionnaire. Am J Epidemiol. 1985;122(1):51-65.
  15. Asghari G, Rezazadeh A, Hosseini-Esfahani F, et al. Reliability, comparative validity and stability of dietary patterns derived from an FFQ in the Tehran Lipid and Glucose Study. Br J Nutr. 2012;108(6):1109-17.
  16. Lopez-Garcia E, Schulze MB, Fung TT, et al. Major dietary patterns are related to plasma concentrations of markers of inflammation and endothelial dysfunction. Am J Clin Nutr. 2004;80(4):1029-35.
  17. Goldberg G, Black A, Jebb S, et al. Critical evaluation of energy intake data using fundamental principles of energy physiology:
    1. Derivation of cut-off limits to identify under-recording. Eur J Clin Nutr. 1991;45(12): 569-81.
  18. Wiedmann T, Minx J. A definition of ‘carbon footprint’. Ecological economics research trends. 2008;1:1-11.
  19. Röös E. Mat-klimat-listan. Uppsala: Dept of Energy and Technology, Sveriges lantbruksuniversitet Rapport (Institutionen för energi och teknik, SLU). 2014:077.
  20. Poe WA, Mokhatab S. Process Optimization. In: Poe WA, Mokhatab S, editors. Modeling, Control, and Optimization of Natural Gas Processing Plants. Boston: Gulf Professional Publishing; 2017:173-213.
  21. Darmon N, Ferguson E, Briend A. Linear and nonlinear programming to optimize the nutrient density of a population's diet: an example based on diets of preschool children in rural Malawi. Am J Clin Nutr. 2002;75(2):245-53.
  22. Omidvar N, Shariat-Jafari S, Minai M, et al. Food-Based Dietary Guidelines. Tehran: Department of Community Nutrition in the Ministry of Health and Medical Education. 2015. [In Persian]
  23. Mahan LK, Raymond JL. Krause's food & the nutrition care process. 4 th ed. St. Louis, Missouri: Elsevier; 2017.
  24. World Health Organization. Protein and amino acid requirements in human nutrition: report of a joint FAO/WHO/UNU expert consultation. [Internet]. World Health Organization; 2007. Available from: https://apps.who.int/iris /handle/ 10665/43411. [Cited Jul 20, 2007].
  25. World Health Organization. Human energy requirements. Report of a Joint FAO/WHO/UNU Expert Consultation, Rome. [Internet]. World Health Organization; 2004. Available from: https:// www.fao.org/3/y5686e/y5686e00.htm. [Cited October 24, 2004].
  26. World Health Organization. Diet, nutrition, and the prevention of chronic diseases: report of a joint WHO/FAO expert consultation. [Internet].  World Health Organization; 2003.  Available from:https://apps.who.int/nutrition /publications/obesity/WHO_TRS_916/en/. [Cited October 24, 2003].
  27. Abdi F, Kashani ZA, Mirmiran P, et al. Investigation and comparison of food consumption pattern in iran and the world: a review article. Journal of Fasa University of Medical Sciences. 2015;5(2):159-67. [In Persian]
  28. Bates B, Lennox A, Prentice A, et al. Headline results from Years 1, 2 and 3 (combined) of the Rolling Programme (2008/2009-2010/11). Department of Health and Food Standards Agency. 2012.
  29. Sáez-Almendros S, Obrador B, Bach-Faig A, et al. Environmental footprints of Mediterranean versus Western dietary patterns: beyond the health benefits of the Mediterranean diet. Environ Health. 2013;12(1):118.
  30. Fiala N. Meeting the demand: An estimation of potential future greenhouse gas emissions from meat production. Ecological Economics. 2008;67(3):412-9.
  31. Hoolohan C, Berners-Lee M, McKinstry-West J, et al. Mitigating the greenhouse gas emissions embodied in food through realistic consumer choices. Energy Policy. 2013;63:1065-74.
  32. Soret S, Mejia A, Batech M, at al. Climate change mitigation and health effects of varied dietary patterns in real-life settings throughout North America. Am J Clin Nutr. 2014;100(suppl_1):490S-495S.
  33. Vieux F, Darmon N, Touazi D, et al. Greenhouse gas emissions of self-selected individual diets in France: Changing the diet structure or consuming less? Ecological economics. 2012;75:91-101.
  34. Pimentel D, Pimentel M. Sustainability of meat-based and plant-based diets and the environment. Am J Clin Nutr. 2003;78(3):660S-3S.
  35. Millward DJ, Garnett T. Plenary Lecture 3 Food and the planet: nutritional dilemmas of greenhouse gas emission reductions through reduced intakes of meat and dairy foods. Proc Nutr Soc. 2010;69(1):103-18.
  36. Eini-Zinab H, Sobhani SR., Rezazadeh A. Designing a healthy, low-cost and environmentally sustainable food basket: an optimisation study. Public Health Nutr. 2021;24(7):1952-61.
  37. Chen C, Chaudhary A, Mathys A. Dietary change scenarios and implications for environmental, nutrition, human health and economic dimensions of food sustainability. Nutrients. 2019:11(4), 856.
  38. Trolle E, Mogensen L, Thorsen AV, et al. Climate friendly dietary guidelines. 9th International Conference on Life Cycle Assessment in the Agri-Food Sector; 2014.
  39. Kerver JM, Yang EJ, Bianchi L, et al. Dietary patterns associated with risk factors for cardiovascular disease in healthy US adults. Am J Clin Nutr. 2003;78(6):1103-10.
  40. Johnston JL, Fanzo JC, Cogill B. Understanding sustainable diets: a descriptive analysis of the determinants and processes that influence diets and their impact on health, food security, and environmental sustainability. Adv Nutr. 2014;5(4):418-29.


Appendix 1: the weight of one serving and recommended serving size of different food pyramid groups 22.
Food groups Recommended serving size The weight of one serving
Bread, Cereal, Rice, & Pasta 6-11 26 g for bread,
75 g for others
Meat, Poultry, Fish, Legumes, Egg, & Nuts 2-3 66 g for meat & poultry,
75 g for fish,
120 g for egg,
114 g for legumes & nuts
Vegetables 3-5 85 g
Fruit 2-4 120 g
Milk, Yogurt, & Cheese 2-3 240 g for milk &yogurt,
52 g for cheese
Fat, Oil, & Sweets Minimum -
Type of Study: Original articles | Subject: Environmental Health, Sciences, and Engineering
Received: 2021/10/26 | Accepted: 2022/01/20 | Published: 2022/03/16

Add your comments about this article : Your username or Email:
CAPTCHA

Send email to the article author


Rights and permissions
Creative Commons License This work is licensed under a Creative Commons Attribution-NonCommercial 4.0 International License.

© 2015 All Rights Reserved | Journal of Environmental Health and Sustainable Development

Designed & Developed by : Yektaweb