Metabolic Food Waste and Ecological Impact of Obesity in FAO World's Region

Introduction

Obesity is a chronic metabolic disorder with a complex etiology representing a remarkable risk factor for the onset of different chronic diseases, such as cardiovascular disease (CVD), diabetes type 2 and cancers, responsible for 60% of deaths worldwide (1). Over the past decade, the obesity burden in western and in developing countries has more than doubled: the WHO estimates that more than 1.9 billion adults and 41 million children under the age of five are overweight or obese (2). Between the different causes, obesity is basically due to an excess consumption of calories over time being turned into body fat, with abdominal fat as a reliable index of negative impacts on health (3). However, obesity condition, other than being an excessive fat deposit, is characterized by excessive and uncontrolled cytokines, free radicals and adhesion molecule production, a condition defined as “low-grade chronic inflammation” associated with the development of degenerative diseases (4, 5). Moreover, due to the uncontrolled high intake of nutritionally unbalanced meals, characterized by elevated caloric, sugars, and fat consumption, obesity condition is also associated with continuous postprandial metabolic stress, characterized by a deep raising of CVD risk factors such as blood pressure, insulin resistance, LDL oxidation, triglycerides and high glucose blood levels.

Consumption of food that is constantly above the recommended calorie requirements by a growing number of people not only represents a risk to health, but it also puts more pressure on natural resources and on the environment (1), including overeating among food waste (6). The calculated progressive increase of food waste suggests that the worldwide obesity epidemic has been the result of a “push effect” of increased food availability and marketing. Since 1974 the energy content of diet has increased 50%, reaching more than 1,400 kcal per person per day or 150 trillion per year (7). In this view, obesity condition represents a considerable cost for the environment (8). Recently, we introduced a new index to calculate the ecological impact of obesity, Metabolic Food Waste [MFW_{(kg of food)}], corresponding to the amount of food leading to Excess Body Fat (EBF) and its impact on the environment expressed as carbon [MFW_(kgCO2eq)], water [MFW_{(×10 L)}], and land footprint [MFW_{(×10 m²)}] (8). We estimated MFW_{(kg of food)} of 63.1 and 127.2 kg per capita in an observational study on 60 overweight and obese subjects, and of 2.081 million kg of food for the Italian population, with the highest contributor from animal products in terms of carbon emissions, water consumption and land use. We claim that increased population adiposity, because of its contribution to climate change from unnecessary food consumption, should be recognized, in addition to being a health and sociological issue, as an environmental problem.

Therefore, the aim of our work is to estimate the MFW_{(kg of food)} in the seven FAO regions and evaluate its impact on climate, water, and land footprints for food commodity groups in order to provide a global picture of the phenomenon.

Materials and Methods

Prevalence of overweight and obesity at a global level from the WHO Global Database on Body Mass Index (BMI) relative to the year 2017 (9) has been used in combination with population data (10) to assess the number of individuals belonging to BMI categories of overweight and obese subjects. In order to assess global Excess Body Fat (EBF) in terms of mass (kg), the difference between average body weight at a national level and “ideal body weight,” given by BMI inverse function, has been calculated. The “ideal BMI” estimated by the midpoint between lowest and highest values using WHO cut-off points for BMI resulted to be 21.7 kg/m² for normal the weight category [(18.5 + 24.9)/2 = 21.7]; while average body height by country was obtained from DHS projects (11) on all completed population-based surveys, the national statistical databases were also used for missing data.

The attained EBF was multiplied for the energy content of 1 kg of body fat (32.2 MJ) to reach the energy from EBF and distributed among the different foods according to their percentage contribution to total energy intake. An estimation of food items contributing to the EBF has been calculated associating energy from EBF with kilocalories from food, determined from the Food Balance Sheets (FBS) in FAOSTAT (12). The percent energy contribution of each food item at the national level was multiplied with the total amount of energy from EBF for each specific country to achieve the amount of energy of each food item contributing to the EBF, with the value translated into amount of food wasted through overweight/obesity [MFW_{(tons of food)}]. Food waste was based on total production through FBS food items grouped into nine main groups: dairy products/milk/eggs, starchy roots, alcoholic beverages, cereals, meat/offals, sugar and sweeteners, fish/seafood, added fats, and pulses. The acquired data allowed us to provide a worldwide estimation of the impact of over-nutrition on planet health through the new index MFW_{(tons of food)} and its impact on the environment as carbon [MFW_(kgCO2eq)], water [MFW_{(m³ water)}], and land footprint [MFW_{(m² land)}] (13, 14). Complete information has been reached for 86 countries, categorized in the seven FAO world regions: Europe (EU), North America and Oceania (NAO), Latin America (LA), Sub-Saharan Africa (SSA), Industrialized Asia (IA), North Africa, West and Central Asia (NAWCA), and South and Southeast Asia (SSEA).

Results

As displayed in Table 1, the overall impact of MFW_{(tons of food)} in the world correspond to 140.7 million tons of food waste associated with overweight and obesity. Between the different regions, Europe (EU) is responsible of the greatest amount of MFW_{(tons of food)} volume (39.2 million tons), followed by North America and Oceania (32.5 million tons) (NAO) and Latin America (20 million tons) (LA), while the lowest extent of MFW was recorded in Sub-Saharan Africa (SSA) with 5 million tons as described in Table 1. It is interesting to note that the highest percentage of MFW_{(tons of food)} in NAO came from obese people (67.7%), however, EU with a similar percentage between OWand OB accounted for the highest volume of MFW.

TABLE 1

Table 1. Metabolic Food Waste [MFW_{(kg of food)}] corresponding to Excess Body Fat by BMI categories (OW, Overweight; OB, Obesity).

As described in Figure 1, dairy products/milk/eggs, were the highest contributor to MFW_{(tons of food)} in the EU (about 12 million tons corresponding to 30.2%) and NAO (33.1%), followed by alcoholic beverages (19.1%) and cereals (16.4%) in EU,meat/offals (15.2%) and alcoholic beverages (13.9%) in NAO. Cereals and dairy products were the two largest contributors to MFW_{(tons of food)} in LA (24.8 and 24.4%, respectively), SSEA (44.6 and 22.8%) and NAWCA (46.0 and 22.2%), while in IA and SSA the highest impact came from cereals (33.8 and 31.5%, respectively) and starchy roots (14.2 and 28.0%).

FIGURE 1

Figure 1. Metabolic Food Waste corresponding to excess body fat from FBS commodities in overweight and obese population expressed as amount of food [MFW_{(kg of food)}]. EU, Europe; NAO, NorthAmerica and Oceania; LA, Latin America; IA, Industrialized Asia; NAWCA, North Africa, West and Central Asia; SSEA, South and Southeast Asia; SSA, Sub-Saharan Africa.

In terms of ecological impact, EU and NAO displayed the highest values for all three MFW footprints (water, land, carbon), about 14 times more than SSA that, as for the MFW_{(tons of food)}, is the area with lowest ecological impact (Table 2). The water footprint for EU and NAO was similar but almost double with respect to LA and 10 times more with respect to the ones with lowest impact (SSA). In terms of GHG emissions, EU was in first place followed by NAO and LA, also here the footprint of EU was almost 10 times more than SSA. Regarding land use, EU was the first followed by NAO and LA, with a land use of about 15 times higher than SSA.

TABLE 2

Table 2. Metabolic Food Waste (MFW) expressed as water (millions m³), GHG emissions (millions kg/CO₂eq), land (millions m²).

Figure 2A shows the contribution of commodities to total GHG emissions by geographical area. Dairy products/milk/eggs and meat/offals have the highest values in EU and NAO, two geographical areas where overweight and obesity are at epidemic proportions, followed by alcoholic beverages. Meat/offals are the highest contributor in IA followed by cereals and fish/seafood, while in LA, SSEA and NAWCA, the first three places were occupied by cereals, dairy products/milk/eggs and meat/offals whereas in SSA cereals were the highest contributor.

FIGURE 2

Figure 2. Metabolic Food Waste corresponding to Excess Body Fat from FBS commodities in overweight and obese population expressed as (A) GHG emission, MFW_{(millions kgCO2eq)}; (B) water consumed, MFW_{(millions m³)}; and (C) land used, MFW_{(millions m²)}. EU, Europe; NAO, North America and Oceania; LA, Latin America; IA, Industrialized Asia; NAWCA, North Africa, West and Central Asia; SSEA, South and Southeast Asia; SSA, Sub-Saharan Africa.

Figure 2B shows total water footprint (as millions m³) from MFW in the seven regions: dairy products/milk/eggs and meat/offals as a whole contribute to more than 70% in EU and NAO. In IA meat/offals was in first place (43.7%), followed by cereals (23.8%). In LA, SSEA, and NAWCA dairy products/milk/eggs and cereals were the two highest contributor to MFW water footprint.

Animal commodities, dairy products/milk/eggs, meat/offals and fish, were the highest contributors to the MFW_{(millions m²)} for land footprint with about 80% of the contribution in EU and NAO, as displayed in Figure 2C. Specifically, dairy products/milk/eggs and meat/offals were at the first two places for all regions, with the only exception of IA where the first contributor to land use was fish/seafood (31.0% against <10% in the other geographical areas). Data on MFW for land footprint does not include alcoholic beverages because they were not available in the footprints database.

Discussion

Obesity is a social challenge that is rising in almost all countries with detrimental effects for human and planet health. In this work we showed that the overall impact of MFW_{(tons of food)} associated with overweight and obesity in the world is 140.7 million tons of food waste, with EU and NAO with the highest ecological impact for water, land and carbon footprints. We proved that obesity burden represents a significant additional increment to the already high global statistics on food wastage causing an unsustainable ecological cost for the planet. However, if we consider that increase in body fat is the result of a long period of reduced physical activity as well as a diet rich in energy-dense food and an intake of calories much higher than metabolic needs, our figuresmight have underestimated the amount of food wasted through the increase in body fat. In order to properly assess the amount of food wasted through obesity, MFW should be calculated in long-term observational/epidemiological studies together with measurements of metabolic parameters.

Our results show that industrialized regions such as EU and NAO display a much higher ecological impact, associated with excess body fat, compared to developing regions like NAWCA and SSA. Our results mirror the main findings from a previous FAO report (15) showing higher values of food waste in the EU and NAO compared to non-industrialized countries, highlighting the responsibility of high-income countries in food waste. It is important to study approaches to address behavior changes in the developed regions, raising the consciousness on the importance of reducing the waste of food and to prefer dietary patterns suited for individual energy needs, to avoid a further increase of the environmental and health impacts associated with unbalanced western dietary habits.

Between the different commodities, meat/offals and dairy products/milk/eggs were shown to be major contributors to MFW_{(tons of food)} and the ecological footprints of EU and NAO and in almost all FAO areas, with few exceptions like cereals in SSEA and NAWCA (Figure 2A). It has been widely shown that animal products have much higher ecological costs compared to plant-based foods (16); however, the role of animal products in people's diet must be carefully considered within the context of each region without neglecting the higher nutritional values of these products for populations suffering from malnutrition. As stated from the EAT-Lancet Commission (17), meat consumption in the world is about 288% times higher than the amount suggested for a balanced and healthy diet. Obviously, reducing meat, dairy, milk, and egg consumption in industrialized countries must be a priority to reduce the ecological burden of animal products.

Finally, it shall be emphasized that our data provide important information because they quantify the effects of over-nutrition on the GHGs emissions, water and land use related to the availability of food at worldwide level, through food balance sheets. However, it must be considered that our results are based on national availability of the main food commodities, providing a valuable insight into diets but not corresponding to average food intake or average food consumption.

Strategies of disease prevention should also be focused on overweight people, representing an excellent target to avoid the development of obesity condition and to minimize the ecological cost of excessive food intake. Overall, we think that it is extremely important to raise awareness in the population at large of the impressive waste of food and natural resources associated with overweight and obesity. At a public health level, it should be highly desirable to develop a specific campaign for obesity prevention focused on increasing physical activity as well as in reducing metabolic food waste through a wise and ethical approach to food consumption.

Conclusion

We provide evidence, at world level, of the enormous amount of food lost through obesity and its ecological impact. As expected, animal products were the highest contributor to MFW; however, large epidemiological studies are needed in order to clearly identify major dietary contributors to MFW in humans. Reducing metabolic food waste associated with obesity will contribute to reducing the ecological impact of unbalanced dietary patterns through an improvement of human health.

Data Availability

The datasets generated for this study are available on request to the corresponding author.

Author Contributions

MS designed the experiment. ET performed data analyses. MS, ET, and CD contributed to data interpretation and manuscript drafting.

Conflict of Interest Statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Abbreviations

GHGs, Greenhouse Gases; MFW, Metabolic Food Waste; EBF, Excess Body Fat; EU, Europe; NAO, North America and Oceania; LA, Latin America; SSA, Sub-Saharan Africa; IA, Industrialized Asia; NAWCA, North Africa, West and Central Asia; SSEA, South and Southeast Asia; CVD, Cardiovascular disease; WHO, World Health Organization; BMI, Body Mass Index; FBS, Food Balance Sheets.

References

1. Barilla Center for Food and Nutrition. Food Waste: Causes, Impacts and Proposals. BCFN. (2012). Available online at: https://www.barillacfn.com/m/publications/food-waste-causes-impact-proposals.pdf

2. World Health Organization (WHO). Overweight and Obesity. (2018). Available online at: https://www.who.int/news-room/fact-sheets/detail/obesity-and-overweight

Google Scholar

3. Hsieh SD, Yoshinaga H. Abdominal fat distribution and coronary heart disease risk factors in men-waist/height ratio as a simple and useful predictor. Int J Obes Relat Metab Disord. (1995) 19:585–9.

PubMed Abstract | Google Scholar

4. Peluso I, Raguzzini A, Villano DV, Cesqui E, Toti E, Catasta G, et al. High fat meal increase of IL-17 is prevented by ingestion of fruit juice drink in healthy overweight subjects. Curr Pharm Des. (2012) 18:85–90. doi: 10.2174/138161212798919020

PubMed Abstract | CrossRef Full Text | Google Scholar

5. Burton-Freeman B, Linares A, Hyson D, Kappagoda T. Strawberry modulates LDL oxidation and postprandial lipemia in response to high-fat meal in overweight hyperlipidemic men and women. J Am Coll Nutr. (2010) 29:46–54. doi: 10.1080/07315724.2010.10719816

PubMed Abstract | CrossRef Full Text | Google Scholar

6. Smil V. Improving Efficiency and reducing waste in our food system. Environ Sci. (2004) 1:17–26. doi: 10.1076/evms.1.1.17.23766

CrossRef Full Text | Google Scholar

7. Hall KD, Guo J, Dore M, Chow CC. The progressive increase of food waste in America and its environmental impact. PLoS ONE. (2009) 4:e7940. doi: 10.1371/journal.pone.0007940

PubMed Abstract | CrossRef Full Text | Google Scholar

8. Serafini M, Toti E. Unsustainability of obesity: metabolic food waste. Front Nutr. (2016) 3:40. doi: 10.3389/fnut.2016.00040

PubMed Abstract | CrossRef Full Text | Google Scholar

9. World Health Organization (WHO). Global Database on Body Mass Index: BMI Classification. Available online at: https://www.who.int/gho/ncd/risk_factors/overweight/en/

10. Food and Agriculture Organization of the United Nations. FAO Statistic Division: Country Indicators. http://www.fao.org/faostat/en/#country

11. Measure DHS. Demographic and Health Surveys. Calverton: ICF International (2012). Available online at: https://dhsprogram.com/

12. Food and Agriculture Organization of the United Nations. FAO Statistic Division. Food Balance Sheets. Available online at: http://faostat3.fao.org/home/E

13. World Wildlife Fund (WWF). Discover the Environmental Cost of Your Household Shopping. (2015). Available online at: http://www.improntawwf.it/carrelloENG/

14. Barilla Center for Food and Nutrition. BCFN4YOU: Calculate Food Impact. (2015). Available online at: https://www.barillacfn.com/en/double_pyramid_technical_data/

15. Gustavsson G, Cederberg C, Sonesson U. Global Food Losses and Food Waste. Rome: Food and Agriculture Organization of the United Nations., FAO (2011). Available online at: http://www.fao.org/docrep/014/mb060e/mb060e00.pdf

16. Barilla Center for Food & Nutrition. Double Pyramid 2016- A More Sustainable Future Depends on Us. 7th ed. Parma: BCFN (2016).

17. 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) 393:447–92. doi: 10.1016/S0140-6736(18)31788-4

PubMed Abstract | CrossRef Full Text | Google Scholar