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OPINION article

Front. Soil Sci., 15 July 2024
Sec. Soil Management

Soil ecology, food systems, and organic waste: the critical network nobody is talking about

  • Warren Alpert Medical School, Brown University, Providence RI, United States

Food change

Why do we care so much about food? On the surface its very simple – we need nutrients for every physiology process but is much more than just fuel. It represents stories passed on from generation to generation, it is at the core of every culture and many social experiences are structured around food. We seek out food and it is integrated in our dopamine reward system. But food has changed dramatically in the past several decades. Modern agriculture and food science practices have dramatically changed what food looks like and there are profound consequences to these changes. Although our biochemical understanding of micronutrient deficiencies has expanded greatly and with modern food science we can now easily and accessibly address these, it has also led to highly palatable energy dense ultra-processed food that is ubiquitous in our society. For example, food swamps are communities that are not close to health food options such as supermarkets and farmers markets, with increased abundance of fast-food restaurants, convenience stores, bodegas (1) which have more energy dense ultra-processed food options than fresh nutrient rich produce (2). Studies have demonstrated a strong association between food swamps and obesity, including being a stronger predictor of obesity than a lack of full-service grocery stores (2). It is no coincidence that the age of access and excess of ultra-processed calorie dense foods has seen alarming trends in obesity (3) and cardiometabolic disease (4). Obesity is a complex multifactorial disease with numerous variables that impact the risk of development and progression including genetics, epigenetics, environmental, and socioeconomic factors, to name a few. Of the factors that contribute to obesity, calorie excess and ultra-processed food consumption are major contributors (5). Our trajectory is deeply concerning with current obesity projections of 1:2 US adults having obesity by 2030 (6). Obesity is linked to significant health care utilization resulting in over 170 billion dollars in associated annual healthcare costs (7).

Soil depletion

Although obesity is one complication of our modern food and agricultural systems, there are many other issues that arise including environmental implications of big/commercial agriculture, chemical fertilizers, synthetic pesticides/herbicides and land being prioritized for domestic livestock. Not only are we eroding our health, but also the world around us. While diets rich in fiber and produce such as the Mediterranean diet are associated with increased gut microbiota diversity (8), emulsifiers which are common food additives in the modern western diet, are associated with reduced microbiota diversity (9). Additionally, some studies demonstrate obesity is associated with a reduced diversity of the gut microbiota (10). Just as our gut microbiota are losing diversity, so too are we seeing loss of biodiversity in numerous other ecosystems including soil resulting in a reduction in functional capacity and ability to tolerate disturbances (11). It is no surprise that our health has diminished as we have replaced plant-based produce with synthetic preservatives, processed grains and refined sugars (12). The soil equally suffers as we apply large batches of chemical fertilizers and pesticides that leads to a reduction in soil biodiversity, and this impacts the health of everything downstream (11). When plants are let to grow as nature intended; in a symbiotic relationship with soil microbes, they produce more health promoting phytochemicals such as flavonoids, as has been demonstrated by the increased production of flavonoids by tomatoes treated with the soil microbe Trichoderma harzianum which has been associated with resistance to fungal infections (13). Unfortunately, as soil microbial biodiversity is reduced, plants become less resilient to the unrelenting external environment such as the ability of plants to prevent disease from pathogens (13, 14). These plants then become reliant on human intervention with application of synthetic pesticides to prevent infestation and disease. Additionally, with modern agricultural practices, there has been an observed reduction in the nutrient density of crops including fruits, vegetables and grains (1517). These less resilient, lower nutrient density plants then enter ours and other food chains with unclear health consequences. Further, we often process these plants into unrecognizable forms which results in further reduction of nutritional quality (18).

Food waste/GHG emissions

Another fundamental component that is critical to consider in this dynamic network is organic waste and greenhouse gas emissions. Greenhouse gases are a major driver of climate change. Methane is a greenhouse gas generated by a variety of processes including the decay of organic waste. It is estimated to account for 12% of the annual greenhouse gas emissions in the United States and is approximately 28 times more potent than carbon dioxide over a 100-year period (19). Approximately 1/3rd of food is wasted annually with a recent EPA report estimating this waste to be in the order of 150 million tons (20). Concerningly, the majority of this food waste is being discarded in landfills, which slowly decays into methane. Although some of this methane is captured and converted to biogas, most of this becomes wasted waste which does not enter back into the ecosystem where it could provide vital nutrients to soil. We also must take into consideration the impact of domestic livestock on greenhouse gas emissions. In the United States, livestock generates up to 1.4 billion tons of manure annually (21), and although this can be used as a soil amendment, large quantities of methane get trapped into the atmosphere as a result. Additionally, approximately 80% of agriculture land is used for domestic livestock worldwide. This includes land used for grazing and growing crops for animal feed (22). Together, food waste and manure production with domestic livestock enteric fermentation account for greater methane emissions than petroleum, natural gas, and coal-based systems annually (23).

Interconnection

We cannot think about these systems in isolation. Each system, including the food system, health system, soil ecological system and climate system, interfaces with one another to generate a dynamic network which we are profoundly disrupting, to the point where each system might not be able to continue compensating. We need to recognize how fundamental these issues are for one world health. Many of these relationships we are disrupting have been established and flourishing for thousands to millions of years and within a few short decades, we think we can miraculously make it better. Of course, our shortsightedness has many unforeseen consequences that are now staring at us in the face. We need to listen to the world around us and not be so limited in our perspective. We as humans have the ability to generate tremendous prosperity, but our suffering continues to grow in the form of debilitating chronic disease as the world around us is also slowly suffering. And while we go on our journey, so much around us is destroyed in the process. We can live in prosperity with all species, and we can heal the environment along with ourselves at the same time.

Possible solutions

By thinking about the soil, we can think of ways to start healing. With sustainable agricultural practices, we can promote soil health while sequestering carbon, a critical endeavor that is on the forefront of most countries policies. We need to give back in a way that replaces what we take. Not in the form of synthetics, but in the form of cover crops, crop rotations, and limited to no till farming, as a few examples, which help to rejuvenate the soil that has been so kind to us. Cover cropping and crop rotations are critical rejuvenation endeavors which help to improve soil architecture, increase fertility including nitrogen fixation with legume intercropping along with prevention of erosion (24). Other powerful benefits of this process have been demonstrated with legumes including increased soil carbon sequestration, microbial biomass (25) and increasing yield of main agricultural cash crops (26). No till farming prevents disturbances to soil and soil architecture allowing for nature to naturally decompose, churn and aerate the soil. This leads to increased water retention capacity of soil, nutrition cycling and retention of organic material (27), while helping to sequester carbon in surface soil (28).

We also have the opportunity to provide the soil with much needed nutrition from organic waste, rather than the commonly applied synthetic petroleum-based chemical fertilizers that are ubiquitous in commercial agriculture. The tremendous amount of food that is wasted annually can be recycled through techniques such as composting and biochar production. Aerobic composting utilizes oxygen to decompose organic waste into a nutrient dense soil amendment which helps to improve soil fertility and structure. Composting also provides increased water absorption and acts as a slowly releasing nutrition reservoir (24). Biochar is generated when organic waste is heated at high temperatures in low oxygen states. This generates a carbon rich highly porous material that offers numerous benefits to soil. Biochar helps to improve the structure of soil including biophysical and biochemical properties. It allows for long term carbon sequestration, it can adsorb heavy metal contaminants and pollutants to reduce entry into our food system, increases soil water retention capacity in part due to the high surface area of the structure, and also promotes increased microbial activity (29). While these are both promising and impactful resources, recycling food waste can go even further including upcycling to repurpose the food and keep it in the food system, a recommendation the EPA thinks needs further attention (30).

Also, continual efforts need to be made to shift our dietary habits to a greater focus on produce allowing us to reduce our reliance on livestock which are major contributors to greenhouse gas emissions. Conceptually, this is a logical and necessary solution, but the applications to achieve this goal are complex and often need to be individualized. Supplemental nutrition assistance programs including Women, Infants and Children (WIC) and National School Lunch Program (NSLP) have been demonstrated to significantly improve diet quality (31). These efforts are important, but as the price of produce continues to increase with inflation, budgetary allocations to programs like this need to be expanded. An example of this in action is the SNAP Eat Well, Be Well Pilot Incentive program which has been implemented statewide in Rhode Island. This incentive program provides $0.50 in SNAP benefits for every $1 spent at participating retailers on qualifying produce (32). Produce prescription programs (PPR) provide prescriptions, vouchers, or gift cards for fruits and vegetables which can be redeemed at grocery stores or farmers markets. PPRs are customarily provided by healthcare providers. PPRs have been demonstrated to improve dietary quality (33, 34) along with enhancing food security (34). Although clinically relevant outcomes have been mixed (33), a recent study demonstrated that PPR significantly reduce blood pressure, BMI and hemoglobin A1C in adults with cardiovascular disease (34). More research needs to be completed on these programs, but efforts like these that help to increase accessibility and affordability of nutrient rich produce is a critical endeavor to make necessary changes for a sustainable future. Other promising efforts include community gardens, urban farms and urban food forests. Community gardens are associated with increased fruit and vegetable consumption (35) along with being associated with a lower BMI than those who do not participate in community gardens (36). Models have demonstrated that urban farms and food forests can generate a significant amount of produce that can provide revenue to the community, aid in urban cooling, and in the case of food forests, they can help to mitigate climate change (37). There is no single solution, but rather numerous collective efforts that are necessary to integrate together in order for us to change our approach to food. And by doing so we can not only change ourselves, but also the world around us.

Collectively, we need to take a step back and think about the relationship of these systems, not individual and isolated systems with rigid boarders, but a dynamic fluid interconnected network. By healing the soil with these practices, we can not only improve the health of plants and organisms that live directly in the soil, which allows for better nutritional quality for plants that enter into our food system, but also increase agricultures yields which helps to improve food security for all. And at the same time, we can increase our ability to combat greenhouse gas emissions and help to rebuild what we have damaged. It is our duty for not just our species, but for all species that call this beautiful planet our collective home.

Author contributions

BP: Writing – original draft, Writing – review & editing.

Funding

The author(s) declare that no financial support was received for the research, authorship, and/or publication of this article.

Conflict of interest

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

Publisher’s note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

References

1. Bevel SM, Tsai MH, Parham A, Andrzejak ES, Jones S, Moore JX. Associations of food deserts and food swamps with obesity-related cancer mortality in the US. JAMA Oncol. (2023) 9:909–16. doi: 10.1001/jamaoncol.2023.0634

PubMed Abstract | CrossRef Full Text | Google Scholar

2. Cooksey-Stowers K, Schwartz MB, Brownell KD. Food swamps predict obesity rates better than food deserts in the United States. Int J Environ Res Public Health. (2017) 14:1336. doi: 10.3390/ijerph14111366

PubMed Abstract | CrossRef Full Text | Google Scholar

3. Fryar CD, Carrol MD, Afful J. Prevalence of overweight, obesity, and severe obesity among adults aged 20 and over: United States 1960-1962 through 2017-2018. Health E-Stats NATIONL CENTER FOR Stat. (2020).

Google Scholar

4. Touvier M, Costa Louzada ML, Mozaffarian D, Baker P, Juul F, Bernard S. Ultra-processed foods and cardiometabolic health: public health policies to reduce consumption cannot wait. Food Thought. (2023) 383:e075294. doi: 10.1136/bmj-2023-075294

CrossRef Full Text | Google Scholar

5. Singh A, Hardin BI, Singh D, Keye D. Epidemiologic and Etiologic Considerations of Obesity. Florida: StatPearls Publishing (2024).

Google Scholar

6. Ward ZJ, Bleich SN, Cradock AL, Barrett JL, Giles CM, Flax C, et al. Projected U.S. State-level prevalence of adult obesity and severe obesity. N Engl J Med. (2019) 381:2440–50. doi: 10.1056/NEJMsa1909301

PubMed Abstract | CrossRef Full Text | Google Scholar

7. Ward ZJ, Bleich SN, Long MW, Gortmaker SL. Association of body mass index with health care expenditures in the United States by age and Sex. PLoS One. (2021) 16:e0247307. doi: 10.1371/journal.pone.0247307

PubMed Abstract | CrossRef Full Text | Google Scholar

8. Khavandegar A, Heidarzadeh A, Angoorani P, Hasani-Ranjbar S, Ejtahed HS, Larijani B, et al. Adherence to the Mediterranean diet can beneficially affect the gut microbiota composition: a systematic review. BMC Med Genomics. (2024) 17:91. doi: 10.1186/s12920-024-01861-3

PubMed Abstract | CrossRef Full Text | Google Scholar

9. Chassaing B, Compher C, Bonhomme B, Liu Q, Tian Y, Walters W, et al. Randomized controlled-feeding study of dietary emulsifier carboxymethylcellulose reveals detrimental impacts on the gut microbiota and metabolome. Gastroenterology. (2022) 162:743–56. doi: 10.1053/j.gastro.2021.11.006

PubMed Abstract | CrossRef Full Text | Google Scholar

10. Pinart M, Dotsch A, Schlicht K, Laudes M, Bouwman J, Forslund SK, et al. Gut microbiome composition in obese and non-obese persons: A systematic review and meta-analysis. Nutrients. (2021) 14:12. doi: 10.3390/nu14010012

PubMed Abstract | CrossRef Full Text | Google Scholar

11. Tibbett M, Fraser TD, Duddiga S. Identifying potential threats to soil biodiversity. PeerJ. (2020) 8:e9271. doi: 10.7717/peerj.9271

PubMed Abstract | CrossRef Full Text | Google Scholar

12. Clemente-Saurez VJ, Beltran-Velasco AI, Redondo-Florez L, Martin-Rodriguez, Tornero-Aguilera JF. Global impacts of western diets and its effects on metabolism and health: A narrative review. Nutrients. (2023) 15:2749. doi: 10.3390/nu15122749

PubMed Abstract | CrossRef Full Text | Google Scholar

13. Jaiswal AK, Mengiste TD, Myers JR, Egel DS, Hoagland LA. Tomate domestication attenuated responsiveness to a beneficial soil microbe for plant growth promotion and induction of systemic resistance to foliar pathogens. Front Microbiol. (2020) 11:604566. doi: 10.3389/fmicb.2020.604566

PubMed Abstract | CrossRef Full Text | Google Scholar

14. Risolil S, Cotrozzi L, Sarrocco S, Nuzzaci M, Pellegrini E, Vitti A. Trichoderma-induced resistance to Botrytis cinerea in Solanum species: A meta-analysis. Plants (Basel). (2022) 11:180. doi: 10.3390/plants11020180

PubMed Abstract | CrossRef Full Text | Google Scholar

15. Davis DR, Epp MD, Riordan HD. Changes in USDA food composition data for 43 garden crops, 1950 to 1999. J Am Coll Nutr. (2004) 23:669–82. doi: 10.1080/07315724.2004.10719409

PubMed Abstract | CrossRef Full Text | Google Scholar

16. Bhardwaj RL, Parashar A, Parewa HP, Vyas L. An alarming decline in the nutritional quality of foods: the biggest challenge for future generations’ Health. Foods. (2024) 13:877. doi: 10.3390/foods13060877

PubMed Abstract | CrossRef Full Text | Google Scholar

17. Hasanaliyeva G, Sufar EK, Wang J, Rempelos L, Volakakis N, Iversen PO, et al. Effects of agricultural intensification on Mediterranean diets: a narrative review. Foods. (2023) 12:3779. doi: 10.3390/foods12203779

PubMed Abstract | CrossRef Full Text | Google Scholar

18. Steele EM, Popkin BM, Swinburn B, Monteiro CA. The share of ultra-processed foods and the overall nutritional quality of diets in the US: evidence from a nationally representative cross-sectional study. Popul Health Metr. (2017) 15:6. doi: 10.1186/s12963-017-0119-3

PubMed Abstract | CrossRef Full Text | Google Scholar

19. Stocker TF, Qin D, Plattner GK, Tignor M, Allen SK, Boschung J, et al. Climate Change 2013: The Physical Science Basis. United Kingdom and New York: IPCC (2013).

Google Scholar

20. EPA. From Farm to Kitchen: The Environmental Impacts of U.S. Food Waste. EPA 600-R21 171 (2021).

Google Scholar

21. Pagliari P, Wilson M, He Z. Animal manure production and utilization: impact of modern concentration animal feeding operations. Anim Manure: Production Characteristics Environ Concerns Manage. (2020) 67. doi: 10.2134/asaspecpub67.c1

CrossRef Full Text | Google Scholar

22. Ritchie H, Roser M. Half of the world’s habitable land is used for agriculture (2019). Available online at: https://ourworldindata.org/global-land-for-agriculture (Accessed 02/28/24).

Google Scholar

23. EPA. U.S. Greenhouse Gas Emissions and Sinks. EPA 430-D-24-001 (2024).

Google Scholar

24. Mohler CL, Johnson SE. Crop rotation and soil tilth, in: Crop Rotations on Organic Farms (2009). Available online at: https://www.sare.org/publications/crop-rotation-on-organic-farms/physical-and-biological-processes-in-crop-production/crop-rotation-and-soil-tilth/ (Accessed 03/05/24).

Google Scholar

25. Li G, Tang X, Hou Q, Li T, Xie H, Lu Z, et al. Response of soil organic carbon fractions to legume incorporation into cropping system and the factors affecting it: a global meta-analysis. Agriculture Ecosyst Environ. (2023) 342:108231. doi: 10.1016/j.agee.2022.108231

CrossRef Full Text | Google Scholar

26. Zhao J, Chen J, Beillouin D, Lambers H, Yang Y, Smith P, et al. Global systematic review with meta-analysis reveals yield advantage of legume-based rotations and its drivers. Nat Commun. (2022) 13:4926. doi: 10.1038/s41467-022-32464-0

PubMed Abstract | CrossRef Full Text | Google Scholar

27. Duyck G, Petit D. Seeing is Believing: Soil Health Practices and No Till Farming Transform Landscapes and Produce Nutritous Food (2019). USDA. Available online at: https://www.usda.gov/media/blog/2016/12/19/seeing-believing-soil-health-practices-and-no-till-farming-transform#:~:text=No%2Dtill%20farming%20increases%20the,reduce%20or%20eliminate%20soil%20erosion (Accessed 03/05/24).

Google Scholar

28. Mondal S, Chakraborty D, Paul RK, Mondal A, Ladha JK. No-till is more of sustaining the soil than a climate change mitigation option. Agriculture Ecosyst Environ. (2023) 351:108498. doi: 10.1016/j.agee.2023.108498

CrossRef Full Text | Google Scholar

29. Yadav SPS, Bhandari S, Bhatta D, Poudel A, Bhattarai S, Yadav P, et al. Biochar application: a sustainable approach to improve soil health. J Agric Food Res. (2023) 11. doi: 10.1016/j.jafr.2023.100498

CrossRef Full Text | Google Scholar

30. EPA. From Field to Bin: The Environmental Impacts of U.S. Food Waste Management Pathways. EPA/600/R-23/065 (2023).

Google Scholar

31. Mande J, Flaherty G. Supplemental Nutritional Assistance Program as a health intervention. Curr Opin Pediatr. (2023) 35:33–8. doi: 10.1097/MOP.0000000000001192

PubMed Abstract | CrossRef Full Text | Google Scholar

32. SNAP Eat Well, Be Well Pilot Incentive Program. STATE OF RHODE ISLAND, Department of Human Services (2024). Available online at: https://dhs.ri.gov/programs-and-services/supplemental-nutrition-assistance-program-snap/supplemental-nutrition-8 (Accessed 04/22/24).

Google Scholar

33. Veldeer S, Scartozzi C, Knehans A, Oser T, Sood N, George DR, et al. A systematic scoping review of how healthcare organizations are facilitating access to fruits and vegetables in their patient populations. J Nutr. (2020) 150:2859–73. doi: 10.1093/jn/nxaa209

PubMed Abstract | CrossRef Full Text | Google Scholar

34. Hager K, Du M, Li Z, Mozaffarian D, Chui K, Shi P, et al. Impact of produce prescriptions on diet, food security, and cardiometabolic health outcomes: a multisite evaluation of 9 produce prescription programs in the United States. Circ Cardiovasc Qual Outcomes. (2023) 16:e009520. doi: 10.1161/CIRCOUTCOMES.122.009520

PubMed Abstract | CrossRef Full Text | Google Scholar

35. Hume C, Grieger JA, Kalamkarian A, D’Onise K, Smithers LG. Community gardens and their effects on diet, health, psychosocial and community outcomes: a systematic review. BMC Public Health. (2022) 22:1247. doi: 10.1186/s12889-022-13591-1

PubMed Abstract | CrossRef Full Text | Google Scholar

36. Zick CD, Smith KR, Kowaleski-Jones L, Uno C, Merril BJ. Harvesting more than vegetables: the potential weight control benefits of community gardening. Am J Public Health. (2013) 103:1110–5. doi: 10.2105/AJPH.2012.301009

PubMed Abstract | CrossRef Full Text | Google Scholar

37. Guerry AD, Hagney M, Janke B, Liu L, Lonsdorf E, Nootenboom C, et al. Vibrant Land: The Benefits of Food Forests and Urban Farms in San Antonio. Canada: Natural Capital Project at Stanford University (2023).

Google Scholar

Keywords: soil, soil ecology, health, food system, food, greenhouse gas, planetary health, climate change

Citation: Perler BK (2024) Soil ecology, food systems, and organic waste: the critical network nobody is talking about. Front. Soil Sci. 4:1403795. doi: 10.3389/fsoil.2024.1403795

Received: 20 March 2024; Accepted: 26 June 2024;
Published: 15 July 2024.

Edited by:

Michelle M. Wander, University of Illinois at Urbana-Champaign, United States

Reviewed by:

Wesley Jarrell, Independent Researcher, Champaign, IL, United States

Copyright © 2024 Perler. 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: Bryce Klein Perler, bryce_perler@brown.edu

Disclaimer: All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.