Sustainable kidney care delivery and climate change – a call to action
Globalization and Health volume 18, Article number: 75 (2022)
The delivery of kidney care, particularly haemodialysis treatment, can result in substantial environmental impact through greenhouse emissions, natural resources depletion and waste generation. However, strategies exist to mitigate this impact and improve long term environmental sustainability for the provision of haemodialysis treatment. The nephrology community has begun taking actions to improve the environmental sustainability of dialysis, but much work remains to be done by healthcare professionals, dialysis providers and professional organisations.
The effects of climate change on global health are increasingly recognised . Global warming, extreme weather events, and many other threats are resulting in changing patterns of disease, with direct and indirect detrimental impact on human health worldwide. Chronic kidney disease (CKD) is increasingly recognised as a global health problem, with an estimated 700 milllion people worldwide living with CKD in 2017 and its prevalence rising 29% between 1990 and 2017 . People living with kidney disease are uniquely vulnerable to the effects of climate change, resulting in rising incidence of heat-related acute kidney injury and CKD, increased risk of nephrolithiasis, vector-borne kidney diseases, and disruption to kidney care delivery associated with extreme weather events (Fig. 1) .
Ironically, the delivery of healthcare is also a significant contributor to greenhouse emissions and natural resources depletion, where it is estimated that almost 5% of the global carbon footprint is produced by the healthcare sector . Greenhouse gas emissions arise directly from healthcare facilities, as well as indirectly from the supply chain of healthcare goods and services. The relative contribution of different clinical areas of the healthcare sector to greenhouse emission is not well studied, but more recent studies have been undertaken to better understand the variability observed [5, 6]. Importantly, variation in greenhouse gas emissions per capita does not correlate highly with health system quality, suggesting that the healthcare sector’s environmental footprint can be reduced without compromising quality. While the global community adopts adaptation and mitigation strategies to minimise the impact of climate change, it is imperative that the medical community limits the carbon footprint of the healthcare sector to move towards a more sustainable healthcare delivery.
The global nephrology community has an important role to play in exploring environmentally sustainable kidney care delivery, especially since the provision of haemodialysis has been highlighted for its disproportionately high and recurrent consumption of water & electrical resources, waste generation and carbon footprint . Moreover, the incidence of dialysis has increased by 43% between 1990 and 2017 , and more than 5 million people globally are estimated to require haemodialysis treatment by 2030, driven by rising prevalence of CKD and its risk factors such as diabetes and obesity . Yet, many healthcare professionals may not realise the enormous scale of environmental impact of haemodialysis, and more importantly, the opportunities that exist for improvement .
Environmental impact of haemodialysis
Water consumption and wastage
The provision of haemodialysis treatment requires large volumes of high-quality water to constitute the dialysate. A typical dialysate flow rate of 500 ml per minute during haemodialysis treatment necessitates 120 l of water over each typical 4-hour session. For a patient on a thrice weekly haemodialysis schedule, this equates to 18,720 l of water per patient annually. Yet, this is an under-estimation of the amount of water used to generate dialysate, as source water typically undergoes reverse osmosis (RO) filtration to remove contaminants. Current RO systems are inefficient; between 50 and 70% of the source water at the RO membrane is rejected. Thus, in a typical 4-hour dialysis session, 240 l of source water is required to prepare the dialysate. Including water required for the pre-treatment priming, rinsing and sterilisation of the system, it has been estimated that water consumption in each session of haemodialysis may be as high as 500 l .
Haemodialysis systems consume large amounts of electrical power to provide equipment start-up, priming, haemodialysis treatment session, rinse and disinfection cycles, and to drive the central RO system. In Australia, the electricity consumption was estimated to be 12.0–19.6 kWh per dialysis treatment session versus 18.7 kWh per day in an average household : a substantial amount considering that each dialysis machine typically provides 2 to 3 treatment sessions per day, six days a week.
Single-use dialysers, blood tubing and dialysate concentrates are often individually packed in plastic and cardboard packaging. It was estimated in one study that each haemodialysis treatment generates 2.5 kg of hazardous waste, of which 38% is plastic . Another study reported up to 8 kg of waste per treatment, of which less than one-third was potentially recyclable .
Although the waste generation, water and power usage during haemodialysis is staggering, there is evidence to suggest that the largest contribution to carbon dioxide (CO2) emission, in fact, arises from pharmaceuticals and medical equipment necessary for haemodialysis. Studies have examined the direct and indirect effect of haemodialysis treatment on CO2 emission (including water, energy, consumables usage, and transportation of staff and patients). In the United Kingdom (UK), haemodialysis is estimated to result in 3.8 tCO2-eq emissions per patient annually , more than 7-fold the mean per patient carbon footprint in UK healthcare . In Australia, haemodialysis treatment alone has been estimated at 10.2 tCO2-eq per patient annually, accounting for more than two-thirds the estimated Australian mean annual per capita CO2 emission of 15.4 tCO2-eq .
There are several areas that can potentially mitigate the environmental impacts of haemodialysis, many of which are ready for immediate adoption, but some require further study (Table 1) . One of the key areas identified is the recycling of RO reject water, since RO reject water has been shown to be as safe as source water, and recycling can be easily accomplished through redirection into storage tanks, instead of drains . Significant reduction in cost of renewable power technology, such as solar rooftops, has made renewable power generation an economically viable option . Retrofitting of heat exchangers to dialysis machines and upgrading to water treatment plants may reduce power and water usage respectively. Lastly, waste segregation, recycling and minimisation, through installation of baling machines to recycle plastic and cardboard, or the use of central delivery of acid for haemodialysis to reduce plastic packaging, have been undertaken.
The consideration of alternative dialytic therapies such as home haemodialysis or peritoneal dialysis may offer some opportunities for reducing the emissions involved with transportation of staff and patients. However, this is quickly offset by the increased frequency and duration of home haemodialysis treatments , and the overall plastic waste generation from peritoneal dialysis .
Challenges & barriers
For many healthcare professionals around the world, the immediate priority is to deliver safe and quality care to patients, with little focus on the associated environmental impact. Even with greater awareness, healthcare professionals may be overwhelmed by information such as “CO2 emission per capita”, or fail to identify the relevance and/or urgency of such issues. Furthermore, the perceived additional costs required to deliver more environmentally friendly care is often a barrier to the adoption of sustainable solutions.
More broadly, people living in low- and middle-income countries (LMICs) are disproportionately susceptible to kidney disease, in part due to contributions from the social determinants of health. Besides an increased prevalence of kidney disease, people in LMICs are further at risk due to limited access to quality kidney care and kidney replacement therapy, resulting in greater health burden and worse outcome. The economic cost of climate change interventions may also be incommensurate to the limited resources faced by LMICs. Yet, people at socioeconomic disadvantage bear the greatest burden of climate change. As an example, kidney disease may be associated with occupations involving exposure to extreme temperatures, such as farming, which are disproportionately held by people in LMICs and/or lower socio-economic status.
Many of the interventions already described utilise existing technology and are easy to implement, with no compromise to delivery of basic healthcare to patients. Collective guidance from professional organisations and coordinated action from industry partners are pivotal to ensure successful implementation of sustainability policies and targeted actions [19, 20]. Moreover, there is evidence that many of the changes that are necessary to improve environmental sustainability in healthcare will also result in significant longer term cost savings and provide financial sustainability over time .
In conclusion, healthcare professionals, dialysis providers and professional organisations should recognise the relevance and urgency of the impact of haemodialysis on climate change and can make immediate and clear contributions towards achieving more sustainable haemodialysis provision and kidney care delivery.
Availability of data and materials
- CO2 :
Chronic kidney disease
Low- and middle-income countries
- UK :
Romanello M, McGushin A, Di Napoli C, Drummond P, Hughes N, Jamart L, et al. The 2021 report of the Lancet Countdown on health and climate change: code red for a healthy future. Lancet. 2021;398(10311):1619–62.
Bikbov B, Purcell CA, Levey AS, Smith M, Abdoli A, Abebe M, et al. 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.
Barraclough KA, Blashki GA, Holt SG, Agar JWM. Climate change and kidney disease-threats and opportunities. Kidney Int. 2017;92(3):526–30.
Lenzen M, Malik A, Li M, Fry J, Weisz H, Pichler PP, et al. The environmental footprint of health care: a global assessment. Lancet Planet Health. 2020;4(7):e271–e9.
Eckelman MJ, Huang K, Lagasse R, Senay E, Dubrow R, Sherman JD. Health Care Pollution And Public Health Damage In The United States: An Update. Health Aff. 2020;39(12):2071–9.
Sehgal A, Slutzman J, Huml A. Sources of Variation in the Carbon Footprint of Hemodialysis Treatment. J Am Soc Nephrol. 2022:ASN.2022010086. Published online ahead of print.
Barraclough KA, Agar JWM. Green nephrology. Nat Rev Nephrol. 2020;16(5):257–68.
Liyanage T, Ninomiya T, Jha V, Neal B, Patrice HM, Okpechi I, et al. Worldwide access to treatment for end-stage kidney disease: a systematic review. Lancet. 2015;385(9981):1975–82.
Yau A, Agar JWM, Barraclough KA. Addressing the Environmental Impact of Kidney Care. Am J Kidney Dis. 2021;77(3):406–9.
Molano-Triviño A, Wancjer B, Neri MM, Karopadi AN, Rosner M, Ronco C. Blue Planet dialysis: novel water-sparing strategies for reducing dialysate flow. Int J Artif Organs. 2018;41(1):3–10.
Hoenich NA, Levin R, Pearce C. Clinical waste generation from renal units: implications and solutions. Semin Dial. 2005;18(5):396–400.
Piccoli GB, Nazha M, Ferraresi M, Vigotti FN, Pereno A, Barbero S. Eco-dialysis: the financial and ecological costs of dialysis waste products: is a 'cradle-to-cradle' model feasible for planet-friendly haemodialysis waste management? Nephrol Dial Transplant. 2015;30(6):1018–27.
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.
Brown LH, Buettner PG, Canyon DV. The energy burden and environmental impact of health services. Am J Public Health. 2012;102(12):e76–82.
Blankestijn PJ. Towards sustainable environmental development in nephrology care, research and education. Nat Rev Nephrol. 2021;17(1):7–8.
Chang E, Lim JA, Low CL, Kassim A. Reuse of dialysis reverse osmosis reject water for aquaponics and horticulture. J Nephrol. 2021;34(1):97–104.
Agar JWM, Perkins A, Tjipto A. Solar-Assisted Hemodialysis. Clin J Am Soc Nephrol. 2012;7(2):310–4.
Chen M, Zhou R, Du C, Meng F, Wang Y, Wu L, et al. The carbon footprints of home and in-center peritoneal dialysis in China. Int Urol Nephrol. 2017;49(2):337–43.
Piccoli GB, Cupisti A, Aucella F, Regolisti G, Lomonte C, Ferraresi M, et al. Green nephrology and eco-dialysis: a position statement by the Italian Society of Nephrology. J Nephrol. 2020;33(4):681–98.
Barraclough KA, Gleeson A, Holt SG, Agar JW. Green dialysis survey: Establishing a baseline for environmental sustainability across dialysis facilities in Victoria, Australia. Nephrology. 2019;24(1):88–93.
Limb M. NHS could save £1bn by adopting green strategies used in kidney units. Bmj. 2013;346:f588.
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Yeo, S.C., Ooi, X.Y. & Tan, T.S.M. Sustainable kidney care delivery and climate change – a call to action. Global Health 18, 75 (2022). https://doi.org/10.1186/s12992-022-00867-9