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Assessment of Mongolian dietary intake for planetary and human health

  • Dashzeveg Delgermaa ,

    Contributed equally to this work with: Dashzeveg Delgermaa, Miwa Yamaguchi

    Roles Data curation, Investigation, Writing – original draft

    Affiliation Department of Public Health Policy Implementation Coordination, National Center for Public Health, Ministry of Health, Ulaanbaatar, Mongolia

  • Miwa Yamaguchi ,

    Contributed equally to this work with: Dashzeveg Delgermaa, Miwa Yamaguchi

    Roles Conceptualization, Formal analysis, Methodology, Project administration, Writing – original draft

    myamaguchi@nibiohn.go.jp

    Affiliation International Center for Nutrition and Information, National Institute of Health and Nutrition, National Institutes of Biomedical Innovation, Health and Nutrition, Tokyo, Japan

  • Marika Nomura,

    Roles Writing – review & editing

    Affiliations International Center for Nutrition and Information, National Institute of Health and Nutrition, National Institutes of Biomedical Innovation, Health and Nutrition, Tokyo, Japan, Human Development Department, Japan International Cooperation Agency (JICA), Tokyo, Japan

  • Nobuo Nishi

    Roles Conceptualization, Funding acquisition, Supervision, Writing – review & editing

    Affiliation International Center for Nutrition and Information, National Institute of Health and Nutrition, National Institutes of Biomedical Innovation, Health and Nutrition, Tokyo, Japan

Abstract

Background

Healthy diets that consider environmental pressures are required to meet sustainable development goals in Mongolia. This study aimed to clarify the extent of planetary and human health on Mongolian dietary intake.

Methods

The intake of eight food groups (g/day) was investigated using the national database of the Household socio-economic survey (HSES) 2019 in Mongolia. The boundary intake of the Planetary health diet (PHD) proposed by the EAT-Lancet Commission was considered 100% adequate. The adequacy (%) of food groups in the HSES were calculated in two areas (urban and rural), during the two seasons (cold and warm), and the total by each boundary of the PHD. The differences between the recommended dietary intake (RDI) in Mongolia and the PHD were also investigated in the same manner.

Results

The adequacy of red meat (i.e., beef, mutton, and horsemeat) in whole areas of Mongolia indicated more than 17 times higher intake (1,738%) than the PHD. The adequacy of vegetables (20%) and fruits (8%) in Mongolia indicated an intake shortage compared to the PHD. These discrepancies in dietary adequacy were greater in rural areas and during the cold seasons than in urban areas and during the warm seasons, respectively. The animal-based protein sources, especially red meat (1,091%), in the RDI of Mongolia were higher than those in the PHD.

Conclusion

This study found a highly excessive intake of red meat and a low intake of vegetables and fruits compared with the PHD among Mongolian people, especially in rural areas and during the cold seasons. The limited diversity of food in severe geographic conditions, poor accessibility of food retailers, and insufficient nutrition education may have led to these results. Therefore, improvements in the food environment and nutritional education are required.

Introduction

Food production negatively influences global environmental change, which threatens food security at the same time [1]. Mongolia has experienced noticeable climate change, with an increase in the average temperature of ≥ 2°C and a decline in rainfall between 1940 to 2015 [2]. Extreme weather, such as drought in summer, results in the loss of livestock and threatens food security and the population’s health [2]. Food production generates greenhouse-gas (GHG) emissions, nitrogen and phosphorus pollution, biodiversity loss, and water and land use [3]. The global GHG emissions from food production include 57% from animal-based food (including livestock feed), 29% from plant-based foods, and 14% from other uses [4].

In addition to securing natural resources, dietary habits are also important when considering population health. In Mongolia, the prevalence of obesity (20.9% in men and 26.5% in women) among adults aged 18 years and older is higher than in the Asian region (17% in men and 20% in women), in addition to the double burden of malnutrition among children and women [5]. Overconsumption of animal-based foods may threaten population health. A review indicated that total protein and animal protein were associated with the risk of cardiovascular diseases and diabetes [6]. Prospective cohort studies and meta-analyses reported that total protein intake was positively associated with all-cause mortality, and higher animal protein intake was associated with mortality from cardiovascular disease [7].

The EAT-Lancet Commission proposed the Planetary health diet (PHD) [3], a framework of planetary boundaries that indicates the intake ranges of food groups to ensure human health and environmental sustainability. The framework recommends the predominant consumption of plant-based foods (vegetables, greens, fruits, and whole grains) and small amounts of animal-based foods (meat, fish, and eggs). This framework has been used in several studies. Studies in Brazil developed the PHD index, confirmed its validity and reliability [8], and found that high adherence to the index was associated with a lower prevalence of obesity [9]. A study in India reported that people consumed cereals, fruits, and vegetables but not enough protein compared with those in the PHD [10]. A study in Denmark proposed the development of a Danish diet adapted to a healthy plant-based diet aligned with the PHD [11]. The benefits of the PHD have been reported not only for health but also for socio-economic reasons. For example, an Australian study reported that a PHD basket was less expensive and more affordable than a typical Australian diet basket [12].

Although some countries have assessed their diets based on the PHD, there is no evidence of the PHD in Mongolia. Traditional Mongolian food is based on the products of nomadic animal herders who raise Mongolian steppe meat and milk [13]. Nomadic culture continues to be practiced in rural areas. Dietary habits in urban areas changed with socio-economic growth, and dietary patterns were positively associated with body mass index [13]. Food consumption is seasonal, particularly in rural areas. Dairy products and meat are highly consumed during winter [14]. In this context, assessing Mongolian diets in urban and rural areas and during cold and warm seasons is needed from the perspective of both planetary and human health.

Therefore, this study aimed to clarify how Mongolian dietary intake was aligned with the PHD using a national survey and compare it between areas (i.e., urban and rural) and seasons (i.e., cold and warm). In addition, to understand the sustainability of national dietary recommendations, this study investigated the differences between national dietary targets and the PHD.

Materials and methods

Study setting

Mongolian dietary intake was investigated using open-source data from the Household socio-economic survey (HSES) performed in 2019 [15]. The health boundary of the PHD was set as the benchmark for dietary intake. The recommended dietary intake (RDI) in Mongolia was used to assess the sustainability of the national dietary recommendations [17].

Household socio-economic survey

Target population.

The HSES is a nationally representative survey that estimates and monitors a country’s level of poverty and people’s living standards. The HSES 2019 was conducted following the procedure of the HSES 2016 [15, 16].This survey used the sampling frame developed by the National Statistics Office, based on population figures obtained from administrative records.

Data collection.

The 936 households were randomly surveyed each month from January 1st 2019 to January 1st 2020, for the HSES 2019, and a total of 11,232 households were selected. Of the total households, 11,197 participated in the survey (99.7% participation rate).

Urban and rural areas were classified according to the following steps. First, geographic domains were classified into four residential zones: Ulaanbaatar as an urban area, and as rural areas, 20 aimag (province) centers, 306 soum centers (i.e., a secondary subdivision outside Ulaanbaatar), and 891 Bags. Second, a primary sampling unit was selected in each zone using the probability proportional estimated size. Finally, 3,600 households in urban areas and 7,597 households in rural areas were randomly chosen from primary sampling units.

The HSES investigated dietary intake during the cold (October to March) and warm (April to September) seasons. However, there was no information on whether dietary intake during the two seasons was investigated in all 11,197 households.

Questionnaires.

The core questionnaire of household socio-economic data and household food consumption was made according to the previous surveys [15, 16]. In the household socio-economic data, to indicate the socio-demographics, this study employed age (18 years and older), sex (men), number of household members (four [median] or more), type of dwelling (Ger), raised or owned livestock (herding, poultry, or any animal) (yes), owned agricultural land (yes), and household enterprise (yes). In the household food consumption, the field offices transmitted the data and provide additional clarification to a survey team in the National Statistics Office through field supervisors. The survey team in the National Statistics Office performed logical and consistent checks for all data. A representative household reported a dietary record and some households were asked to revise their answers whenever the field office found an error. A 30-day dietary record compiled by a researcher every 10 days, three times during a single month, was recorded to capture the household’s food consumption in urban areas. A 7-day dietary record was administered to all provinces in rural areas using the following question: “how much food item have you consumed in total during the past 7 days?” In both urban and rural areas, the household representative answered the question, “did you or any member of your household spend the following items during the past month/ or the past 7 days?” If the answer was “no,” the major place of “restaurants, cafes” or “canteens in schools, works canteens” was selected.

EAT-Lancet reference diet

This study used the PHD as a reference diet to assess the dietary intake of Mongolian [3]. The PHD indicated the scientific targets and ranges of intake of 11 food groups (e.g., 300 g/day ranged from 200 to 600 g/day in all vegetables), added fats (unsaturated and saturated oils), and added sugars (all sugars) per 2,500 kcal/day of total energy. In addition, six food groups (beef, lamb, and pork; chicken and other poultry; eggs; fish; legumes; and nuts) were included as protein sources.

Recommended dietary intake in Mongolia

The RDI in Mongolia indicates the daily target consumption of meat, meat products, flour, bakery products and various types of rice based on the average daily consumption in Mongolians [17]. The targets of total daily energy intake and energy from fat and nutrients (i.e., unsaturated and saturated fats) were referenced according to the human energy requirement in 2001/2002 proposed by the Ministry of Health in Mongolia [18].

Food groups

This study classified food items of the HSES 2019 based on the food-based dietary guidelines “Ger” into the PHD food groups (Table 1) [19]. The national food guide is designed to shape a Mongolian wooden tent “Ger.” The food guide is divided into three food group layers: cereals and cereal products are placed at the bottom of the tent; vegetables, meat, fish, and eggs are placed at the second level; and fruits and dairy products are placed at the final level [19]. Although the EAT-Lancet Commission named the food group “beef, lamb, and pork” red meat [20], beef, mutton, horse meat, and camel meat are among the major red meats in Mongolia [15]. Therefore, this study changed the name to “red meat” to be understandable. Confectionery products and sugar were included in the “added sugar” in the PHD food group since the HSES indicated the intake of the two foods as one food group. We did not classify whole grains because the information was not available in the HSES.

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Table 1. Classification of food items in the household socio-economic survey based on the planetary health diet.

https://doi.org/10.1371/journal.pgph.0001229.t001

Data analysis

Socio-demographics.

The proportion of people aged 18 years and older and men was calculated by individuals. The proportion of four or more household members, Ger of dwelling, raised or owned livestock, owned agricultural land, and household enterprise was calculated per household. The result was shown as a whole area because no data were available on the living areas (i.e., urban and rural) in which the houesholds lived.

Adequacy of dietary intake against the PHD.

The health boundary and range (g/day) of each food group against 2,500 (kcal/day) proposed by the PHD were converted by the total energy intake (3,085 kcal/day) among Mongolian people aged 18 years and older. The adequacy (%) of each food group was calculated by dividing dietary intake (g/day) by the converted health boundary (g/day). Similarly, we calculated the health boundary, range, and adequacy in two areas (urban and rural), during the two seasons (warm and cold), and the RDI in Mongolia using each dietary (g/day) and energy intake (2,863 kcal/day in urban areas, 3,529 kcal/day in rural areas, 3,057 kcal/day during the cold season, 3,111 kcal/day during the warm season, and 2,400 kcal/day in the RDI in Mongolia). The food groups of chicken and other poultry, egg, fish, legumes, and nuts were not used in these two areas because this information was not presented in the database. For the same reason, this study did not use nuts in either season or RDI in Mongolia.

Ethics.

This study used tabulated and published information on the HSES. The National Statistics Office obtained informed consent from the household representatives.

Results

Characteristics of the population

The 64% of individuals in the households were over 18 years (48% men) (Table 2). Over half of households lived with four or more members, and 41% of them lived in Ger. The 34% and 5.5% of households possessed the livestock and agricultural land, respectively. A household enterprise was present in 12% of households.

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Table 2. Household characteristics in the household socio-economic survey.

https://doi.org/10.1371/journal.pgph.0001229.t002

Dietary intake in whole and two areas in comparison to the PHD

Table 3 compares Mongolian dietary intake with the PHD in whole areas, urban areas, and rural areas. In whole areas, one of the major differences between the two diets was red meat which was more than 17 times higher intake (300 g/day, 1,738% adequacy) in Mongolia than that recommended by the PHD (17 g/day ranged from 0 to 35 g/day). On the other hand, all vegetables and fruits in Mongolia were lower (73 g/day, 20% adequacy in all vegetables and 20 g/day, 8.1% adequacy in all fruits) than these in the PHD (370 g/day ranged from 247 to 740 g/day in all vegetables and 247 g/day ranged from 123 to 370 g/day in all fruits). Other food groups indicated 100% and more adequacy (105–146% adequacy) but almost within the range of each PHD, except for unsaturated oils (13% adequacy). High intake of red meat and low intake of all vegetables and fruits were more evident in rural areas than urban areas.

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Table 3. Mongolian dietary intake compared with the health boundary of the planetary health diet and the adequacy in total and two areas.

https://doi.org/10.1371/journal.pgph.0001229.t003

Dietary intake during two seasons in comparison to the PHD

The differences in dietary intake during the cold and warm seasons compared to the PHD are shown in Table 4. The adequacy of red meat during the cold season (324 g/day, 1,905% adequacy) was higher than that during the warm season (313 g/day, 1,812% adequacy). On the other hand, other consumptions of protein sources, such as chicken and other poultry, fish, and legumes during the cold and warm seasons were lower (0.2–15% adequacy) than those in the PHD, except for eggs (86% adequacy during the cold season and 97% adequacy during the warm season).

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Table 4. Mongolian dietary intake compared with the health boundary of the planetary health diet and the adequacy during the two seasons.

https://doi.org/10.1371/journal.pgph.0001229.t004

National dietary recommendations in comparison to the PHD

The RDI in Mongolia, compared with the PHD, is presented in Table 5. The three most abundant protein sources were red meat (120 g/day, 1,091% adequacy), eggs (20 g/day, 200% adequacy), and chicken and other poultry (40 g/day, 182% adequacy). The adequacy of other protein sources ranged from 70% to 143%. RDIs in all protein sources were within the range of each PHD, except for red meat (120 g/day in RDI in Mongolia and 0–21 g/day in the PHD). All vegetables and fruits in the RDI in Mongolia were 260 g/day (113% adequacy) and 200 g/day (131% adequacy), respectively, and were within the range of each PHD (153–459 g/day for all vegetables and 77–230 g/day for all fruits).

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Table 5. Recommended dietary intake in Mongolia compared with the health boundary of the planetary health diet.

https://doi.org/10.1371/journal.pgph.0001229.t005

Discussion

This study clarified that Mongolian people have an extremely high intake of red meat and a low intake of vegetables and fruits based on the PHD recommendations. These results were more evident in rural areas and during the cold season than in urban areas and during the warm season, respectively. This is the first study to indicate the extent of the discrepancy between the current Mongolian dietary intake and the PHD for planetary and human health.

The present results of high consumption of red meat and low consumption of vegetables and fruits were similar to the global trend [20], except for countries such as India where a vegetarian diet is practiced [10]. Nevertheless, the discrepancy observed in this study was much larger than the global trend [20], Brazil [9], and Denmark [11]. Furthermore, the population intake of red meat, vegetables, and fruits did not meet the RDI in Mongolia in the present study. Among multifactorial interactions, such as limited food availability and accessibility, a lack of nutrition and health knowledge is likely to be a key factor in these results. A review found success in increasing vegetables and fruits intake in many countries by improving nutrition education [21]. A basic and robust system to disseminate nutrition education is required to reach the target of RDI in Mongolia. A study reported that even medical professionals lacked accurate knowledge of the recommended daily salt intake (5 g/day) [22]. Therefore, accurate nutrition education considering sustainable healthy diets to health professionals and communities is required to nudge them to choose healthier and more sustainable food.

This study showed that a high intake of red meat and dairy products and a low intake of vegetables and fruits were more evident in rural areas than urban areas. A similar result was reported in the previous study that a “Nomadic” dietary pattern indicated a high consumption of dairy products, milk, red meat, and refined grains, and low juice and sugar-sweetened beverages, processed meat, and fruit [13]. In addition, the Nomadic pattern was associated with increased iron and zinc intake and decreased fiber intake [13]. Nomadic dietary patterns may result in obesity and a high risk of cardiovascular diseases [6, 7]. According to the geographic characteristics in this study, people living with four or more family members in Ger and owning livestock are likely to have traditional dietary habits. As rural populations practice, traditional Mongolian diets are characterized by a high intake of dairy products (i.e., milk and natural yogurt), fats and oil, sugar, confectionery, and horsemeat [15]. In addition, nomadic herders usually feed themselves, especially on meat and dairy products [13]. These traditional dietary cultures imply that the limited accessibility, availability, and affordability of food retail and variety of food, such as fresh vegetables and fruits, are present in rural areas compared with urban areas.

The environmental impact may differ between urban and rural areas. The GHG emissions from livestock, mainly consumed in urban areas, come from several sources, such as emissions related to feed (e.g., fertilizer and land use), processing, transport, on-farm energy use, and enteric fermentation [23]. The environmental impact generated by livestock and wild game consumed by self-sufficiency in rural areas may be lower than that generated by livestock consumed by people in urban areas, even if there is high consumption of red meat in rural areas.

A higher intake of red meat during the cold season than during the warm season would have a specific background in a severe climate. During the coldest season, the traditional dietary pattern of high red meat (i.e., horsemeat) and fats is usually consumed [24], especially in rural areas, to preserve sufficient energy reserves at severe temperatures [14]. Therefore, the difference in dietary intake between the two seasons should be considered a strategy for sustainable healthy diets.

In this study, animal-based protein sources in the RDI in Mongolia were higher than those in the PHD, particularly red meat. Studies in America and Italy have reported differences between national dietary guidelines and the PHD due to their dietary habits and traditional cultures [25, 26]. A review suggested that national food-based dietary guidelines could be sustainable and healthy to some extent, even if dietary goals are not completely aligned with global health and environmental targets [27]. A new RDI in Mongolia may be required to originally achieve planetary and human health with consideration of feasibility, such as food culture, geographic characteristics, and food variety.

This study did not indicate the intake of whole grains due to the limited information from the HSES. A study reported that the usual mean intake (g/2,500kcal/day) of whole grains (ranging from 2.2 to 20) was lower than that of refined grains (ranging from 361 to 461) in eight provinces in Mongolia [13]. The consumption of refined grains, such as bread, pasta, and rice, may be associated with westernization [15].

The present results are generalizable because this study used an open-source national survey [15]. However, this study has some limitations that warrant mention. First, this study did not include food groups because the lack of information. The intake of whole grains has not been investigated in the HSES and the RDI in Mongolia. Some protein sources in two areas (i.e., chicken and other poultry, eggs, fish, legumes, and nuts) and during the two seasons (i.e., nuts) were investigated but not published in detail. Furthermore, the results of added sugar did not reflect only sugar intake, as this study included confectionery products. The fifth National Nutrition Survey reported the nutritional status of the Mongolian population but did not publish data on food-based dietary consumption [28]. More data should be considered in future studies to clarify the overall status of food intake. Second, the different processes of the 30-day dietary record in urban areas and the 7-day dietary record in rural areas made precise comparison between the two areas difficult. The survey in rural areas was conducted using simple methods compared to urban areas because of the limited resources for the survey, such as manpower. Third, this study did not necessarily adapt Mongolian food culture to the PHD, such as the characteristics of dietary cultures and food availability. The EAT-Lancet Commission recommends the local interpretation and adaptation of the universally applicable PHD [20]. According to the RDI in Mongolia [17], the recommended intake of red meat in the PHD may not be feasible for Mongolian diets. Fourth, the PHD targeted adults aged 18 years and older. Given that the data were available, the interpretation classified by sex and age group (i.e., children and older adults) would differ from the present results. Fourth, the assessment of sustainable healthy diets in Mongolia was indecisive only from this study, using one measurement. The measurement of GHG emissions, water and land use, and nitrogen and phosphorus fertilizer application may help us deeply understand this comprehensive assessment.

Conclusions

This study indicated an extremely high intake of red meat and a low intake of vegetables and fruits compared to the recommended intake of the PHD among Mongolian people. This discrepancy was larger in rural areas and during the cold season than in urban areas and during the warm season, respectively. To prevent health inequality due to the geographic and seasonal situation of planetary and human health, further policies for multi-sectoral interventions, such as fields of infrastructure and education systems, are required to improve the accessibility, availability, and affordability of healthy food, as well as nutrition education.

References

  1. 1. Myers SS, Smith MR, Guth S, Golden CD, Vaitla B, Mueller ND, et al. Climate Change and Global Food Systems: Potential Impacts on Food Security and Undernutrition. Annu Rev Public Health. 2017;38:259–277. pmid:28125383
  2. 2. The World Bank Group and the Asian Development Bank. Climate Risk Country Profile: Mongolia. The World Bank Group and the Asian Development Bank. 2021. Available from: https://www.adb.org/sites/default/files/publication/709901/climate-risk-country-profile-mongolia.pdf
  3. 3. Willett W, Rockström J, Loken B, Springmann M, Lang T, Vermeulen S, et al. Food in the Anthropocene: the EAT-Lancet Commission on healthy diets from sustainable food systems. Lancet. 2019;393:447–492. pmid:30660336
  4. 4. Xu X, Sharma P, Shu S, Lin TS, Ciais P, Tubiello FN, et al. Global greenhouse gas emissions from animal-based foods are twice those of plant-based foods. Nature Food. 2021;2:724–732.
  5. 5. Minister of Health in Mongolia, The National Center for Public Health, and World Health Organization. Fourth national STEPS Survey on Prevalence of Noncommunicable Disease and injury Risk Factors-2019. World Health Organization. 2020. Available from: https://cdn.who.int/media/docs/default-source/ncds/ncd-surveillance/data-reporting/mongolia/mongolia-steps-survey—2019_brief-summary_english.pdf?sfvrsn=5ba7a1d3_1&download=true
  6. 6. Mariotti F. Animal and Plant Protein Sources and Cardiometabolic Health. Adv Nutr. 2019;10:S351–s66. pmid:31728490
  7. 7. Chen Z, Glisic M, Song M, Aliahmad HA, Zhang X, Moumdjian AC, et al. Dietary protein intake and all-cause and cause-specific mortality: results from the Rotterdam Study and a meta-analysis of prospective cohort studies. Eur J Epidemiol. 2020;35:411–429. pmid:32076944
  8. 8. Cacau LT, De Carli E, de Carvalho AM, Lotufo PA, Moreno LA, Bensenor IM, et al. Development and Validation of an Index Based on EAT-Lancet Recommendations: The Planetary Health Diet Index. Nutrients. 2021;13. pmid:34067774
  9. 9. Cacau LT, Benseñor IM, Goulart AC, Cardoso LO, Lotufo PA, Moreno LA, et al. Adherence to the Planetary Health Diet Index and Obesity Indicators in the Brazilian Longitudinal Study of Adult Health (ELSA-Brasil). Nutrients. 2021;13. pmid:34835947
  10. 10. Sharma M, Kishore A, Roy D, Joshi K. A comparison of the Indian diet with the EAT-Lancet reference diet. BMC Public Health. 2020;20:812. pmid:32471408
  11. 11. Lassen AD, Christensen LM, Trolle E. Development of a Danish Adapted Healthy Plant-Based Diet Based on the EAT-Lancet Reference Diet. Nutrients. 2020;12. pmid:32168838
  12. 12. Goulding T, Lindberg R, Russell CG. The affordability of a healthy and sustainable diet: an Australian case study. Nutr J. 2020;19:109. pmid:32998734
  13. 13. Bromage S, Daria T, Lander RL, Tsolmon S, Houghton LA, Tserennadmid E, et al. Diet and Nutrition Status of Mongolian Adults. Nutrients. 2020;12. pmid:32456038
  14. 14. Food and Agriculture Organization of the United Nations. FAO/UNICEF/UNDP Report: Joint Food Security Assessment Mission to Mongolia. Food and Agriculture Organization of the United Nations. 2007. Available from: https://www.fao.org/3/j9883e/j9883e00.htm
  15. 15. The National Statistical Office of Mongolia. Household Socio-economic survey 2019; 2022 [cited 2022 June 16]. Database: Statistical Microdata [Internet]. Available from: http://web.nso.mn/nada/index.php/catalog/HSES
  16. 16. The National Statistics Office of Mongolia. Household Socio Economic Survey 2016; 2019 [cited 2022 July 24]. Database: International Household Survey Network [Internet]. Available from: https://catalog.ihsn.org/catalog/8346/study-description
  17. 17. Nutrition department, National Center for Public Health, Ministry of Health in Mongolia. The recommended dietary intake in Mongolia. 2021 [cited 2022 June 16]. In: legalinfo.mn [Internet]. Ulaanbaatar: Interactive. Available from: https://legalinfo.mn/mn/detail?lawId=207686&showType=1 (in Mongolian)
  18. 18. Nutrition department, National Center for Public Health, Ministry of Health in Mongolia. Human energy requirement. 2021 [cited 2022 June 16]. In: legalinfo.mn [Internet]. Ulaanbaatar: Interactive. Available from: https://legalinfo.mn/mn/detail/12552. (in Mongolian)
  19. 19. Nutrition department, National Center for Public Health, Ministry of Health in Mongolia. Food-based dietary guidelines–Mongolia. 2022 [cited 2022 June 16]. In: Food-based dietary guidelines [Internet]. Rome: FAO. Available from: https://www.fao.org/nutrition/education/food-based-dietary-guidelines/regions/countries/mongolia/fr/.
  20. 20. EAT-Lancet Commission. Summary Report of the EAT-Lancet Commission, Healthy Diets From Sustainable Food Systems. EAT-Lancet Commission. 2019 [cited 2022 June 16]. In: The EAT-Lancet Commission on Food, Planet, Health [Internet]. Stockholm: EAT. Available from: https://eatforum.org/eat-lancet-commission/eat-lancet-commission-summary-report/.
  21. 21. Pem D, Jeewon R. Fruit and Vegetable Intake: Benefits and Progress of Nutrition Education Interventions- Narrative Review Article. Iran J Public Health. 2015;44:1309–1321. pmid:26576343
  22. 22. Hikita N, Batsaikhan E, Sasaki S, Haruna M, Yura A, Oidovsuren O. Factors Related to Lacking Knowledge on the Recommended Daily Salt Intake among Medical Professionals in Mongolia: A Cross-Sectional Study. Int J Environ Res Public Health. 2021;18. pmid:33916892
  23. 23. Barthelmie. Impact of Dietary Meat and Animal Products on GHG Footprints: The UK and the US. Climate 2022; 10:43. https://doi.org/10.3390/cli10030043
  24. 24. Dugee O, Khor GL, Lye MS, Luvsannyam L, Janchiv O, Jamyan B, et al. Association of major dietary patterns with obesity risk among Mongolian men and women. Asia Pac J Clin Nutr. 2009;18:433–40. pmid:19786392
  25. 25. Blackstone NT, Conrad Z. Comparing the Recommended Eating Patterns of the EAT-Lancet Commission and Dietary Guidelines for Americans: Implications for Sustainable Nutrition. Curr Dev Nutr. 2020;4:nzaa015. pmid:32154501
  26. 26. Tucci M, Martini D, Del Bo C, Marino M, Battezzati A, Bertoli S, et al. An Italian-Mediterranean Dietary Pattern Developed Based on the EAT-Lancet Reference Diet (EAT-IT): A Nutritional Evaluation. Foods. 2021;10. pmid:33800396
  27. 27. Springmann M, Spajic L, Clark MA, Poore J, Herforth A, Webb P, et al. The healthiness and sustainability of national and global food based dietary guidelines: modelling study. BMJ. 2020;370:m2322. pmid:32669369
  28. 28. Ministry of Health, National Center for Public Health, UNICEF. Nutrition Status of the Population of Mongolia, Fifth National Nutrition Survey Report. UNICEF; 2017. Available from: https://www.unicef.org/mongolia/media/1116/file/NNS_V_undsen_tailan_EN.pdf