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Renal health benefits of sustainable diets in Japan: a review

Abstract

Global warming may reduce food production and force people to adopt dietary habits of inadequate quantity or quality. Such dietary habits could trigger chronic kidney disease through inappropriate nutrition or lifestyle diseases. Livestock farming and other types of food production are responsible for many greenhouse gases. These problems are being emphasized as a diet-environment-health trilemma to be addressed on a global scale, with various methods being proposed toward its resolution. Diets like plant-based and low-protein diets not only potentially prevent the progression of chronic kidney disease, but are also rational from an environmental preservation perspective. Evidence from Japan on resolutions for this trilemma is sparse, but one concrete proposal is the use of traditional Japanese diets like washoku, the Okinawa diet, and the traditional Buddhist diet. However, traditional Japanese diets also have several problems, such as excessive salt content and caloric deficiencies, and need to be modified and incorporated into the current lifestyle. The progression of chronic kidney disease needs to be prevented with appropriate dietary treatment and environmental friendly manner.

Introduction

The number of individuals with chronic kidney disease (CKD) is steadily increasing worldwide [1,2,3]. As a human economic activity, medical practice consumes various resources and impacts the environment and is estimated to account for 3–10% of all economic activity [4,5,6,7,8]. With the progression of CKD, increases are seen in medical expenses for medication, visits to doctors, and hospitalization [9], naturally resulting in greater greenhouse gas emissions (GHGE). In particular, dialysis treatment that is essential for prolonging the life of individuals with end-stage kidney disease uses vast amounts of electricity, water, and plastics and is estimated to have about ten times the environmental impact of the average per-person medical activities [10]. The burden on the global environment, primarily from GHGE, further exacerbates global warming and produces various health problems, such as cardiovascular complications, respiratory disease, and mental disorders [11, 12]. Global warming may result in the onset or progression of CKD through a variety of mechanisms [13]. As a direct cause, repeated acute kidney injury due to heat stress may result in chronicity of renal impairment, or trigger rhabdomyolysis or urolithiasis involve in development of CKD. Possible indirect causes are dehydration due to water shortages, tubular damage from contamination by nephrotoxic pesticides, insecticides, or heavy metals, and vector-borne illnesses such as malaria and dengue fever [14]. Combined with typical causes of CKD, such as chronic glomerulonephritis, hypertension and diabetes, global warming has been suggested to potentially lead to an increase in the prevalence of CKD.

According to a Japan-wide statistical survey conducted at the end of 2019, diabetes and hypertensive nephropathy (nephrosclerosis) were the top one and two most common primary diseases, respectively, for newly starting dialysis therapy [15]. Chronic glomerulonephritis was previously the most common and is not a lifestyle disease, and moved to third most common [15]. This indicates a change in disease structure among renal diseases, such as an increase in lifestyle-related diseases. This is consistent with the current situation that in recent years, food habits around the world have been becoming more westernized [16], resulting in increased intake of animal protein as well as cardiovascular complications [17, 18]. Empirically, limiting salt and protein intake has been shown to help prevent the onset of uremia [19]. While randomized controlled trials (RCTs) on educational interventions such as diet management and nutritional counseling are relatively difficult to conduct, limiting the possibility of accumulating high-quality evidence, experience leaves little doubt that nutritional counseling is an important part of CKD treatment.

If there is indeed an effect of global warming from the increase in GHGE caused by CKD treatment, as suggested above, food supply problems could result due to issues such as smaller crop yield, declining livestock production, and declining fish catch rates. However, most of current studies have not been able to directly quantify how much climate change will affect food yields, because it was forecasted by various uncertain anthropogenic factors [20]. Environmental issues stemming from medical practices are therefore linked to diet and nutritional problems, as well as renal health problems, with interactions among the three types of problems likely. This diet-environment-health trilemma [20] should be addressed at the global level (Fig. 1). From a nephrology perspective, the environmental impact of dialysis treatment plays a strong role in this trilemma. Japan is the 5th highest producer of GHGE in the world [21] and has 344,000 patients on maintenance dialysis [15] and so has a great responsibility to combat the problem. In this review, we discuss how to achieve nutritional treatment that effectively prevents the onset and progression of CKD and a diet with less environmental impact in Japan.

Fig. 1
figure 1

The diet-environment-health trilemma is superimposed by dialysis therapy for patients with end-stage kenal disease. Diet and nutrition, health, and the environment all mutually interact. When focusing on kidney health, maintenance dialysis is essential for individuals with end-stage kenal disease and generates health care-related greenhouse gas emissions (GHGE). Drugs, hospitalization, capital investment, labor costs, water, electricity, waste, and plastics should all be recognized as having environmental impacts

Diet-environment axis: temporal changes in Japanese diets and GHGE

Dining tables in modern Japan are covered with foods made using various ingredients and methods. Ingredients can be broadly categorized as animal- or plant-based, with the former considered to produce far higher GHGE [20, 22,23,24]. Cows, sheep, and other ruminant species produce methane (CH4) and release particularly high GHGE [20, 22]. The food industry accounts for a high ratio of GHGE, so choosing a plant-based diet is a plausible way to improve the global environment [24, 25]. While the traditional Japanese diet (washoku) is plant-based and less processed food [26], intake of animal-based foods has increased from 114.9 g/day in 1955 to 338.7 g/day in 2019 and the processed food consumption ratio was 43.0% in 1990 and 50.5% in 2010, predicted to increase to 58.9% in 2035 [27]. This diversification of diets in modern Japan, and especially the westernization of diet and overconsumption of processed foods, is expected to have impacts on both health and the environment. Furthermore, in addition to food production activities such as crop and livestock farming, Japan’s unique situation as a country with a low food self-sufficiency rate must be considered. Life cycle assessment (LCA) is a method for calculating various human economic activities (Fig. 2) [23, 24, 28]. For example, following a diet requires producing ingredients, transporting those ingredients, processing them into food products, and preparing them for meals. This entire process has environmental impacts, most notably from GHGE. The GHGE from importing and domestic transport processes cannot be overlooked [23, 29]. For this reason, evidence on LCA from other countries does not fit Japan as is, and making calculations and resolutions based on the specific characteristics of Japan, including diet, is important. In LCA research comparing modern Japanese-style, Chinese-style, and Western-style cuisines in Japan, ingredient procurement and preparation calculations have shown that Japanese-style meals have the lowest GHGE, although the differences are not dramatic (Table 1) [30]. This may be partially attributable to the use of many imported products and processed foods in modernized Japanese foods. Traditional Japanese diets are shown in Table 2. Unfortunately, no LCA studies on these traditional diets have been conducted. Japanese-style cuisine (washoku) is high in fish and soybean consumption and low in animal fat and meat consumption. In Okinawa, which used to have the longest lifespan, people ate a sweet potato-heavy diet with small amounts of pork (a monogastric animal) that likely had low GHGE. In Japan and other countries in Asia where Mahayana Buddhism spread, a certain proportion of the population was vegan and people followed a traditional Buddhist diet that likely produced very low GHGE [31]. However, as shown in the data for a strict traditional Buddhist diet in Table 2, energy and nutrients are supplemented as needed. Based on the above, when considering how to reduce GHGE, using washoku with domestically produced plant-based ingredients and incorporating a traditional Japanese diet may make rational sense from an LCA perspective.

Fig. 2
figure 2

Life cycle assessment in actual food production. In dietary life, greenhouse gases include gases like CO2, methane (CH4), nitric oxide (N2O), and chlorofluorocarbons (CFCs) and are produced in various processes (called the “life cycle”). Greenhouse gas emissions (GHGE) produced in resource preparation, material production and transportation, food processing, cooking, and waste disposal are calculated as stacked CO2-equivalents impacting global warming. For example, Diet A has an environmental impact from material production but a far lower impact from transportation than Diet B. As a result, Diet A is a better diet from an environmental preservation perspective when considering the entire life cycle. The carbon footprint that is used as a scale is called a midpoint indicator as it does not directly affect humankind

Table 1 Environmental impact of the modern diet
Table 2 Nutritional comparison of the average diet of a modern Japanese person and traditional Japanese diets

Adapted and modified from Toshie Tsuda et al. Life cycle CO2 assessment associated with model menu in Japanese household. Journal of Life Cycle Assessment Japan. 2007;3(3):157–67 [31] with permission. Abbreviations: GHGE, greenhouse gas emissions.

Diet-health axis: role of diets in chronic kidney disease

The importance of dietary treatment in renal disease has long been debated [32]. A low-salt diet not only can help prevent the onset or exacerbation of hypertension and the onset of cardiovascular complications, but also may mitigate renal dysfunction and reduce urinary protein [33]. Excessive protein intake leads to uremic symptoms, and a protein-restricted diet is believed to have preventive effect on CKD [19]. Though it has been still clinically controversial that low-protein diets prevent or attenuate the progression of CKD, a general population-based observational study demonstrated people who consumed more protein from red and processed meats were at an increased risk of developing CKD [34] and end-stage kidney disease [35]. On the other hand, CKD risk was significantly lower among those who had a higher consumption of nuts and legumes suggesting plant protein offers advantages over animal protein in patients with CKD [36]. In the case of mild CKD, active intake of potassium can help prevent the development of cardiovascular complications and hypertension [37, 38]. Examples of typical diets for implementing such dietary treatment are traditional diets such as the Mediterranean diet and the Okinawa diet [38] and diets based on clinical research and/or academic society recommendations, such as the Dietary Approaches to Stop Hypertension [39] or a protein-restricted diet [40]. Common points for all these diets are the plant-based nature with low salt and protein contents, and high potassium content. A search of the literature regarding the relationship between progression of CKD and nutritional education interventions gives 494 hits, including 22 RCTs. As expected, most interventions involved restriction of protein or salt, but evidence on the Mediterranean diet was also included [41,42,43] (Fig. 3). Among all races, the Japanese, both men and women, have long life expectancies, and evidence suggests that traditional Japanese diets can prolong life and reduce the risks of cardiovascular complications [44, 45]. However, scientific evidence is currently lacking on progression of CKD as an outcome of intervention with a traditional Japanese diet (Fig. 3). Conversely, as increased potassium intake in advanced renal disease can carry a risk of cardiac death from hyperkalemia, nutritional treatment requires considerations by specialists. In recent years, CKD patients have become older, so careful nutritional guidance is also required. For older adults, excessive salt or protein restriction can lead to frailty and may aggravate prognosis.

Fig. 3
figure 3

Current evidence of dietary intervention to prevent progression of CKD. A keyword search identified 494 publications in PubMed. Of those, 22 were RCTs matching the outcome of preventing progression of CKD, and 16 were systematic reviews or meta-analyses. Of those, none provided direct evidence on traditional Japanese diets

To summarize, while a number of issues require caution, plant-based diets generally offer clear benefits in preventing the onset and progression of CKD [38]. Although following a vegan diet is difficult in modern Japan, increasing the proportion of plant-based foods in a diet is possible with nutritional counseling. Moreover, traditional Japanese diets also have several problems, which are listed as caloric deficiencies, excessive salt content (Table 2) and reduced satisfaction and quality of life due to unfitting modern society. Therefore, the traditional diets may need to be modified into diets balancing environmental sustainability and renal health based on recent nutritional science in CKD. However, the effects of a traditional Japanese diet on CKD have not been tested, and epidemiological and clinical evidence is needed.

Environment-health axis: life cycle impact assessment for better understanding of environmental issues by health care providers

Of the axes in the trilemma, we discussed the effects of diet on health in the previous section. In contrast, it is more difficult for medical professionals to understand the effects of the environment on health. The GHGE often used to assess environmental impact do not directly affect humans and are therefore called a midpoint indicator. Medical professionals have very few opportunities to imagine the effects of GHGE on the patients they are seeing in daily practice. On the other hand, end point environmental indicators in LCA include “monetary cost” and “health” that affect people [46]. These are areas of interest in medical economics and public health science and can be easily understood by medical professionals. As LCA research has progressed in recent years, various methods of assessment have been established, such as Life cycle Impact assessment Method based on End point modeling (LIME), which can assess damage to health and economic impact [47]. Carbon footprint research into dialysis for end-stage kidney disease has been ongoing since around 2010 and has shown the production of massive amounts of GHGE due to the use of a vast quantity of resources, including drugs, electricity, water, and plastics [10, 48,49,50]. We recently used LIME to measure the monetary loss and health damage of resource consumption with a dialysis treatment model as an end point environmental indicator that surpasses midpoint indicators [51]. Considering a treatment model in which one patient on maintenance hemodialysis visits the hospital three times a week for 4 h of a dialysis session, we calculated a health damage of 2.4 × 10−3 disability-adjusted life years and environmental load equivalent to the monetary loss of 85.6 USD per year. Based on this result, 1 year of treatment for 418 patients on maintenance hemodialysis was equivalent to the loss of 1 year of healthy life for 1 person on earth. Importantly, this result ignores the health gained by the person on dialysis and therefore we never intend to deny dialysis treatment itself. The basic data used in the calculations were data used in other industries and agriculture, and the results are merely theoretical figures under a treatment model, and not actual measurements. The result may therefore be an under- or overestimation. That said, this is the first example showing that consumption of vast resources in medical practice damages human health.

Co-benefits of Japanese traditional diets on environment preservation and renal health

Resolving the diet-environment-health trilemma posed for renal health care requires the procurement and preparation of ingredients with a low environmental impact, nutritional treatments that effectively protect renal function, and wide acceptance of both in Japan as the dietary culture. In addition, reducing the number of people with CKD and the number of people on maintenance dialysis requires modification of patients, health care professionals, and the society that supports them. One useful method may be to scientifically determine what would be most effective for achieving both environmental and health benefits using quantitative LCA results [22, 23, 52,53,54]. We are currently speculating on whether a plant-based diet centered around domestically produced ingredients can improve both GHGE and CKD in Japan. However, it needs the environmental impact of domestic production must not exceed that of imports. To examine the possibilities, further development of LCA-based calculation methods is necessary.

Some specific plant-based diets are the traditional washoku diet, the Okinawa diet, and the traditional Buddhist diet. Using domestically produced foods reduces the need for transport, preserves links to ancient life history and culture, and may boost agriculture and the food industry in Japan. The low food self-sufficiency rate in Japan is related to the high cost of domestically produced food and policy issues related to trade. Unfortunately, for us, it has not been possible to estimate that food self-sufficiency in Japan would reliably reduce the environmental burden. Even though maintaining domestic food production may be more expensive than imported agricultural products in the short term, the long-term cost of maintaining domestic production is actually lower when the cost of the contingency of “not being able to buy food with your money” should be also taken into account. On the negative side, inadequate nutritional controls can cause frailty in older adults due to low protein intake or may trigger hyperkalemia in people with end-stage kidney disease. Furthermore, excessive salt content of traditional Japanese diet and lack of energy in traditional Buddhist diet are not acceptable levels. Nevertheless, if some issues and problems can be overcome and modified as “sustainable diets in Japan,” traditional Japanese diets may reduce both the carbon footprint and the prevalence of lifestyle-related diseases as midpoints. In advance of this, our team had started promotion of Japanese diets in new era, that is summarized by reducing the amount of salt by using dashi (Japanese soup stock). The achievement was released by the International Society of Renal Nutrition and Metabolism [55]. Conceivable end points are protection of biodiversity, improvements in land use with structural changes to agriculture, suppression of increases in the prevalence of end-stage kidney disease, reductions in medical costs, and improvements in both the global environment and human health (Fig. 4).

Fig. 4
figure 4

Putative effects of Japanese traditional diets on end point over midpoint in planetary and human boundaries. Plant-based, low-protein diets as the traditional washoku diet, the Okinawa diet, and the traditional Buddhist diet. Using domestically produced foods reduces the need for transport, preserves links to ancient life history and culture, and may boost agriculture and the food industry in Japan. However, excessive food restrictions can cause frailty in older adults due to inadequate protein intake or trigger hyperkalemia among individuals with end-stage kidney disease due to potassium loading. Therefore, traditional diets should be modified toward co-benefit of renal health and environment. Traditional Japanese diets and sustainable diets in Japan may reduce the carbon footprint and reduce the prevalence of lifestyle diseases as midpoints. As end points, these diets may benefit the global environment or help prevent the progression of end-stage kidney disease

Table 3 summarizes the relationship between diet and environment, between diet and renal health, and between the environment that is far removed from medical professionals and renal health. We consider resolving this trilemma for renal health could possibly improve the prognosis for people with CKD. Hopefully, this debate about renal health will have ripple effects on other medical fields and bring us closer to resolving the diet-environment-health trilemma in Japan.

Table 3 Initiative for mitigating the Diet-Environment-Renal Health trilemma in Japan

Conclusion

As global warming progresses, renal health sector, without exception from other industries, will require effort to reduce GHGE. Doctors, other health care specialists must work together to try to prevent the progression of CKD for reducing the need of resource-hungry therapy for end-stage kidney disease. Traditional Japanese diets may offer a rational solution to the diet-environment-health trilemma. However, traditional Japanese diets also have several problems, such as excessive salt content, and need to be modified and incorporated into the current lifestyle as sustainable diets in Japan.

Availability of data and materials

Not applicable.

Abbreviations

CKD:

Chronic kidney disease

GHGE:

Greenhouse gas emission

RCT:

Randomized control trial

LCA:

Life cycle assessment

References

  1. GBD Chronic Kidney Disease Collaboratio. Global, regional, and national burden of chronic kidney disease, 1990–2017: a systematic analysis for the Global Burden of Disease Study 2017. Lancet. 2020;395(10225):709–33.

    Article  Google Scholar 

  2. Couser WG, Remuzzi G, Mendis S, Tonelli M. The contribution of chronic kidney disease to the global burden of major noncommunicable diseases. Kidney Int. 2011;80(12):1258–70.

    PubMed  Article  Google Scholar 

  3. Nagai K, Asahi K, Iseki K, Yamagata K. Estimating the prevalence of definitive chronic kidney disease in the Japanese general population. Clin Exp Nephrol. 2021;25(8):885–92.

    PubMed  Article  Google Scholar 

  4. Nansai K, Fry J, Malik A, Takayanagi W, Kondo N. Carbon footprint of Japanese health care services from 2011 to 2015. Resour Conserv Recycl. 2020;152:104525.

    Article  Google Scholar 

  5. Chung JW, Meltzer DO. Estimate of the carbon footprint of the US Health Care Sector. JAMA. 2009;302(18):1970–2.

    CAS  PubMed  Article  Google Scholar 

  6. Eckelman MJ, Sherman JD, MacNeill AJ. Life cycle environmental emissions and health damages from the Canadian healthcare system: an economic-environmental-epidemiological analysis. PLoS Med. 2018;15(7):e1002623-e.

    Article  CAS  Google Scholar 

  7. Malik A, Lenzen M, McAlister S, McGain F. The carbon footprint of Australian health care. Lancet Planet Health. 2018;2(1):e27–35.

    PubMed  Article  Google Scholar 

  8. Wu R. The carbon footprint of the Chinese health-care system: an environmentally extended input-output and structural path analysis study. Lancet Planet Health. 2019;3(10):e413–9.

    PubMed  Article  Google Scholar 

  9. Nagai K, Iseki C, Iseki K, Kondo M, Asahi K, Saito C, et al. Higher medical costs for CKD patients with a rapid decline in eGFR: a cohort study from the Japanese general population. PLoS ONE. 2019;14(5):e0216432.

    CAS  PubMed  PubMed Central  Article  Google Scholar 

  10. Lim AEK, Perkins A, Agar JWM. The carbon footprint of an Australian satellite haemodialysis unit. Aust Health Rev. 2013;37(3):369–74.

    PubMed  Article  Google Scholar 

  11. Nagai K, Barraclough K, Ueda A, Itsubo N. Sustainability in dialysis therapy: Japanese local and global challenge. Renal Replace Ther. 2021;7(1):42.

    Article  Google Scholar 

  12. Watts N, Adger WN, Agnolucci P, Blackstock J, Byass P, Cai W, et al. Health and climate change: policy responses to protect public health. Lancet. 2015;386(10006):1861–914.

    PubMed  Article  Google Scholar 

  13. Johnson RJ, Stenvinkel P, Jensen T, Lanaspa MA, Roncal C, Song Z, et al. Metabolic and kidney diseases in the setting of climate change, water shortage, and survival factors. J Am Soc Nephrol. 2016;27(8):2247–56.

    PubMed  PubMed Central  Article  Google Scholar 

  14. Barraclough KA, Agar JWM. Green nephrology. Nat Rev Nephrol. 2020;16(5):257–68.

    PubMed  Article  Google Scholar 

  15. Report ADD. JSDT renal data registry. J Jpn Soc Dial Ther. 2020;53(12):579–632 (in Japanese).

    Article  Google Scholar 

  16. Kearney J. Food consumption trends and drivers. Philos Trans R Soc Lond B Biol Sci. 2010;365(1554):2793–807.

    PubMed  PubMed Central  Article  Google Scholar 

  17. Al-Shaar L, Satija A, Wang DD, Rimm EB, Smith-Warner SA, Stampfer MJ, et al. Red meat intake and risk of coronary heart disease among US men: prospective cohort study. BMJ. 2020;371:m4141.

    PubMed  PubMed Central  Article  Google Scholar 

  18. Bellavia A, Stilling F, Wolk A. High red meat intake and all-cause cardiovascular and cancer mortality: is the risk modified by fruit and vegetable intake? Am J Clin Nutr. 2016;104(4):1137–43.

    CAS  PubMed  Article  Google Scholar 

  19. Piccoli GB, Capizzi I, Vigotti FN, Leone F, D’Alessandro C, Giuffrida D, et al. Low protein diets in patients with chronic kidney disease: a bridge between mainstream and complementary-alternative medicines? BMC Nephrol. 2016;17(1):76.

    PubMed  PubMed Central  Article  CAS  Google Scholar 

  20. Tilman D, Clark M. Global diets link environmental sustainability and human health. Nature. 2014;515(7528):518–22.

    CAS  PubMed  Article  Google Scholar 

  21. International Energy Agency (IEA) - CO2 Emissions from Fuel Combustion Highlights (2020 Edition).https://www.iea.org/data-and-statistics/data-product/greenhouse-gas-emissions-from-energy-highlights. Accessed 01 Dec 2021

  22. Xu X, Sharma P, Shu S, Lin T-S, Ciais P, Tubiello FN, et al. Global greenhouse gas emissions from animal-based foods are twice those of plant-based foods. Nat Food. 2021;2(9):724–32.

    CAS  Article  Google Scholar 

  23. Poore J, Nemecek T. Reducing food’s environmental impacts through producers and consumers. Science. 2018;360(6392):987–92.

    CAS  PubMed  Article  Google Scholar 

  24. Springmann M, Clark M, Mason-D’Croz D, Wiebe K, Bodirsky BL, Lassaletta L, et al. Options for keeping the food system within environmental limits. Nature. 2018;562(7728):519–25.

    CAS  PubMed  Article  Google Scholar 

  25. Crippa M, Solazzo E, Guizzardi D, Monforti-Ferrario F, Tubiello FN, Leip A. Food systems are responsible for a third of global anthropogenic GHG emissions. Nat Food. 2021;2(3):198–209.

    CAS  Article  Google Scholar 

  26. Gabriel AS, Ninomiya K, Uneyama H. The role of the Japanese traditional diet in healthy and sustainable dietary patterns around the world. Nutrients. 2018;10(2):173.

    PubMed Central  Article  CAS  Google Scholar 

  27. Ministry of Agriculture, Forestry and Fisheries of Japan. Future estimation of food consumption in Japan (2019 edition), https://www.maff.go.jp/j/press/kanbo/kihyo01/190830.html. Accessed 01 Dec 2021 (in Japanese)

  28. Itsubo N, Inaba A. A new LCIA method: LIME has been completed. Int J Life Cycle Assess. 2003;8(5):305.

    Article  Google Scholar 

  29. Escobar N, Tizado EJ, zu Ermgassen EKHJ, Löfgren P, Börner J, Godar J. Spatially-explicit footprints of agricultural commodities: mapping carbon emissions embodied in Brazil’s soy exports. Global Environ Change. 2020;62:102067.

    Article  Google Scholar 

  30. Tsuda T, Kubokura T, Tsujimoto S, Ueda R, Ohya C. Life cycle CO2 assessment associated with model menu in Japanese household. J Life Cycle Assess Jpn. 2007;3(3):157–67.

    Article  Google Scholar 

  31. Tseng AA. Equivalent reduction in greenhouse gas emissions by Mahayana Buddhists practicing vegetarian diets. J Relig Health. 2020;59(1):598–613.

    PubMed  Article  Google Scholar 

  32. Addis T, Lew W. Diet and death in acute uremia. J Clin Invest. 1939;18(6):773–5.

    CAS  PubMed  PubMed Central  Article  Google Scholar 

  33. McMahon EJ, Campbell KL, Bauer JD, Mudge DW, Kelly JT. Altered dietary salt intake for people with chronic kidney disease. Cochrane Database Syst Rev. 2015;6(2):CD010070.

    Google Scholar 

  34. Haring B, Selvin E, Liang M, et al. Dietary protein sources and risk for incident chronic kidney disease: results from the atherosclerosis risk in communities (ARIC) study. J Ren Nutr. 2017;27(4):233–42.

    CAS  PubMed  PubMed Central  Article  Google Scholar 

  35. Lew QJ, Jafar TH, Koh HW, et al. Red meat intake and risk of ESRD. J Am Soc Nephrol. 2017;28(1):304–12.

    PubMed  Article  Google Scholar 

  36. Kelly JT, Carrero JJ. Dietary sources of protein and chronic kidney disease progression: the proof may be in the pattern. J Ren Nutr. 2017;27(4):221–4.

    PubMed  Article  Google Scholar 

  37. Burnier M. Should we eat more potassium to better control blood pressure in hypertension? Nephrol Dial Transplant. 2019;34(2):184–93.

    CAS  PubMed  Article  Google Scholar 

  38. Carrero JJ, González-Ortiz A, Avesani CM, Bakker SJL, Bellizzi V, Chauveau P, et al. Plant-based diets to manage the risks and complications of chronic kidney disease. Nat Rev Nephrol. 2020;16(9):525–42.

    PubMed  Article  Google Scholar 

  39. Appel LJ, Moore TJ, Obarzanek E, Vollmer WM, Svetkey LP, Sacks FM, et al. A clinical trial of the effects of dietary patterns on blood pressure. N Engl J Med. 1997;336(16):1117–24.

    CAS  PubMed  Article  Google Scholar 

  40. Okada H, Yasuda Y, Kashihara N, Asahi K, Ito T, Kaname S, et al. Essential points from evidence-based clinical practice guidelines for chronic kidney disease 2018. Clin Exp Nephrol. 2019;23(1):1–15.

    Article  Google Scholar 

  41. Díaz-López A, Becerra-Tomás N, Ruiz V, Toledo E, Babio N, Corella D, et al. Effect of an intensive weight-loss lifestyle intervention on kidney function: a randomized controlled trial. Am J Nephrol. 2021;52(1):45–58.

    PubMed  Google Scholar 

  42. Di Iorio BR, Marzocco S, Bellasi A, De Simone E, Dal Piaz F, Rocchetti MT, et al. Nutritional therapy reduces protein carbamylation through urea lowering in chronic kidney disease. Nephrol Dial Transplant. 2018;33(5):804–13.

    PubMed  Article  CAS  Google Scholar 

  43. Mekki K, Bouzidi-bekada N, Kaddous A, Bouchenak M. Mediterranean diet improves dyslipidemia and biomarkers in chronic renal failure patients. Food Funct. 2010;1(1):110–5.

    CAS  PubMed  Article  Google Scholar 

  44. Ikeda N, Saito E, Kondo N, Inoue M, Ikeda S, Satoh T, et al. What has made the population of Japan healthy? Lancet. 2011;378(9796):1094–105.

    PubMed  Article  Google Scholar 

  45. Kurotani K, Akter S, Kashino I, Goto A, Mizoue T, Noda M, et al. Quality of diet and mortality among Japanese men and women: Japan Public Health Center based prospective study. BMJ. 2016;352:i1209-i.

    PubMed  PubMed Central  Article  CAS  Google Scholar 

  46. Nagai K, Suzuki H, Ueda A, Agar JWM, Itsubo N. Assessment of environmental sustainability in renal healthcare. J Rural Med. 2021;16(3):132–8.

    PubMed  PubMed Central  Article  Google Scholar 

  47. Tang L, Ii R, Tokimatsu K, Itsubo N. Development of human health damage factors related to CO2 emissions by considering future socioeconomic scenarios. Int J Life Cycle Assess. 2018;23(12):2288–99.

    CAS  Article  Google Scholar 

  48. Agar JWM. Green dialysis: the environmental challenges ahead. Semin Dial. 2015;28(2):186–92.

    PubMed  Article  Google Scholar 

  49. Connor A, Lillywhite R, Cooke MW. The carbon footprint of a renal service in the United Kingdom. QJM Int J Med. 2010;103(12):965–75.

    CAS  Article  Google Scholar 

  50. Connor A, Lillywhite R, Cooke MW. The carbon footprints of home and in-center maintenance hemodialysis in the United Kingdom. Hemodial Int. 2011;15(1):39–51.

    PubMed  Article  Google Scholar 

  51. Nagai K, Itsubo N. Environmental impact of care for end-stage kidney disease on the earth and humans. JMA J. 2022;5(1):109–13.

    PubMed  Article  Google Scholar 

  52. Jarmul S, Dangour AD, Green R, Liew Z, Haines A, Scheelbeek PF. Climate change mitigation through dietary change: a systematic review of empirical and modelling studies on the environmental footprints and health effects of “sustainable diets.” Environ Res Lett. 2020;15:123014.

    PubMed  PubMed Central  Article  Google Scholar 

  53. 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(10170):447–92.

    PubMed  Article  Google Scholar 

  54. Stylianou KS, Fulgoni VL, Jolliet O. Small targeted dietary changes can yield substantial gains for human health and the environment. Nature Food. 2021;2(8):616–27.

    Article  Google Scholar 

  55. Japanese kidney-friendly recipes. How to make DASHI and basic Japanese foods? The International Society of Renal Nutrition and Metabolism, https://www.isrnm.org/post/japanese-kidney-friendly-recipes-how-to-make-dashi-and-basic-japanese-foods. Accessed 13 May 2022

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Acknowledgements

We would like to thank Rieko Uchima for helping us to determine the contents of the traditional Okinawa diet as a nutrition specialist.

Funding

This article was supported, in part, by Japan Society for the Promotion of Science Grant Nos. 18KK0431 and 19K17729 and by the Japanese Association of Dialysis Physicians Grant No. 2019-1.

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KN wrote the manuscript. KS and YK contributed to construct tables and figures and reviewed the manuscript. NI supervised the descriptions regarding life cycle assessment and reviewed the manuscript. All authors edited and approved the final manuscript.

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Correspondence to Kei Nagai.

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Nagai, K., Kosaka, S., Kawate, Y. et al. Renal health benefits of sustainable diets in Japan: a review. Ren Replace Ther 8, 25 (2022). https://doi.org/10.1186/s41100-022-00415-6

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Keywords

  • Chronic kidney disease
  • Sustainability
  • Life cycle assessment