ORIGINAL ARTICLES


Environmental impact of a tele-screening program for diabetic retinopathy in rural argentina
Tomás Ortiz-Bassoa-b, María Florencia Ricardb-c, María Soledad Córdobad, Ariel Paladinie


aIMTIB. CONICET. Instituto Universitario Hospital Italiano de Buenos Aires, Buenos Aires, Argentina.
bUniversidad Nacional de La Pampa, Santa Rosa, Argentina.
cSubsecretaría de Cambio Climático, Gobierno de La Pampa, Santa Rosa, Argentina.
dCentro Oftalmológico Venero, Santa Rosa, La Pampa, Argentina.
eDirección de Atención Primaria y Gestión Sanitaria, Ministerio de Salud de La Pampa, Argentina.


Oftalmol Clin Exp (ISSNe 1851-2658)
2024; 17(1): eXX-eXX.


Abstract
Background: Tele-screening programs for diabetic retinopathy are implemented worldwide, but the environmental impact has not been studied yet. The aim of this study was to evaluate the emission reduction achieved by a tele-screening program for diabetic retinopathy in La Pampa (Argentina).
Methods: A descriptive study was performed comparing the emissions generated with and without the program. A retinal camera was transported to 60 rural cities, and the images were classified asynchronously as “referable” and “non-referable”. An ophthalmologist then traveled to each location to assess the identified “referable” cases. The eqCO2 emissions generated by the program were compared with those that patients would have generated if they had traveled from their location to the nearest ophthalmology center in the conventional manner.
Results: Emissions generated per patient without the program were equivalent to 63 kg, whereas with program implementation they ranged from 4 kg to 18 kg. The reduction in emissions per patient for 2019, 2020, and 2021 was 45 kg, 41 kg, and 62 kg, respectively. The absolute reduction in eqCO2 emissions by the program for 2019, 2020, and 2021 was 166Tn, 28Tn, and 161Tn, respectively.
Conclusion: CO2 emissions were significantly reduced by the tele-screening program for diabetic retinopathy prevention in La Pampa. Ophthalmologists should consider the environmental impact when implementing their practice.
Keywords: diabetic retinopathy, telemedicine, environmental pollution, carbon footprint, global warming.

Impacto ambiental de un programa de telescreening de retinopatía diabética en argentina.
Resumen
Objetivo: La expansión mundial de programas de tele-screening para la retinopatía diabética ha demostrado su eficacia en diversas regiones; sin embargo, su impacto ambiental permanece insuficientemente examinado. Este estudio se propuso cuantificar la disminución en las emisiones de carbono atribuible a la implementación de un programa de tele-screening para la retinopatía diabética en La Pampa, Argentina.
Materiales y métodos: Mediante un diseño descriptivo comparativo, este estudio evaluó las emisiones de equivalentes de dióxido de carbono (eqCO2) generadas por el desplazamiento de pacientes con y sin la operación del programa. Se utilizó una cámara retinal móvil para examinar a pacientes en 60 localidades rurales, clasificando las imágenes obtenidas en “referibles” y “no referibles” para posterior evaluación oftalmológica presencial en casos seleccionados. Las emisiones se estimaron comparando el eqCO2 producido por el programa frente al que hubieran emitido los pacientes al trasladarse al centro oftalmológico más cercano por medios convencionales.
Resultados: Sin la intervención del programa, las emisiones por paciente se estimaron en 63 kg de eqCO2, mientras que su implementación redujo este valor a un rango entre 4 y 18 kg por paciente. Durante los años 2019, 2020 y 2021 se logró una reducción de emisiones por paciente de 45 kg, 41 kg y 62 kg, respectivamente, lo que resultó en una disminución absoluta de emisiones de 166 toneladas, 28 toneladas y 161 toneladas de eqCO2 por año, respectivamente.
Conclusión: La implementación del programa de tele-screening para la retinopatía diabética en La Pampa ha demostrado una significativa reducción en las emisiones de eqCO2, subrayando la importancia de considerar el impacto ambiental en la práctica oftalmológica. Este estudio destaca el potencial de las intervenciones de telemedicina para contribuir a la sostenibilidad ambiental en el sector salud.
Palabras clave: retinopatía diabética, telemedicina contaminación ambiental, huella de carbono, calentamiento global.

Impacto ambiental de um programa de teletriagem de retinopatia diabética na Argentina
Resumo
Objetivo: A expansão global dos programas de teletriagemda retinopatia diabética demonstrou a sua eficácia em diversas regiões; no entanto, o seu impacto ambiental continua insuficientemente examinado. Este estudo teve como objetivo quantificar a diminuição das emissões de carbono atribuíveis à implementação de um programa de teletriagem para retinopatia diabética em La Pampa, Argentina.
Materiais e métodos: Utilizando um desenho descritivo comparativo, este estudo avaliou as emissões de equivalentes de dióxido de carbono (eqCO2) geradas pela movimentação de pacientes com e sem operação do programa. Uma câmera retinal móvel foi utilizada para examinar pacientes em 60 localidades rurais, classificando as imagens obtidas em “refernciáveis” e “não referenciáveis” para posterior avaliação oftalmológica presencial em casos selecionados. As emissões foram estimadas comparando o eqCO2 produzido pelo programa versus aquele emitido pelos pacientes quando se deslocam até o centro oftalmológico mais próximo por meios convencionais.
Resultados: Sem a intervenção do programa, as emissões por paciente foram estimadas em 63 kg de eqCO2, enquanto a sua implementação reduziu esse valor para um intervalo entre 4 e 18 kg por paciente. Durante os anos de 2019, 2020 e 2021, foi alcançada uma redução nas emissões por paciente de 45 kg, 41 kg e 62 kg, respetivamente, resultando numa diminuição absoluta das emissões de 166 toneladas, 28 toneladas e 161 toneladas de eqCO2 por ano, respectivamente.
Conclusão: A implementação do programa de teletriagem para retinopatia diabética em La Pampa demonstrou uma redução significativa nas emissões de eqCO2, ressaltando a importância de considerar o impacto ambiental na prática oftalmológica. Este estudo destaca o potencial das intervenções de telemedicina para contribuir para a sustentabilidade ambiental no setor da saúde.
Palavras-chave: retinopatia diabética, telemedicina, poluição ambiental, pegada de carbono, aquecimento global.


Introduction
In recent decades, the world has experienced an enormous number of environmental disasters, largely due to increasing global warming. The consequences, such as polar ice retreat, heat waves, wildfires, droughts, and floods are some of the events that threaten not only human health, but also the future of the next generations1. In response to these challenges, the United Nations forged the Paris Agreement in 2016, aiming to mitigate the rise in global temperature and address climate change concerns2.
While efforts to combat climate change primarily focus on reducing industrial emissions, it is essential to recognize the role of various sectors, including healthcare, in minimizing their carbon footprint. The healthcare sector is responsible for approximately 5% of global greenhouse gas emissions3. The United States healthcare system alone is responsible for an 8% increase in carbon footprint4. One of the measures that has a negative impact is the alarming increase in hazardous waste generated by healthcare systems5. Additionally, the necessity of medical visits often entails long-distance travel, resulting in harmful emissions that negatively impact the environment6.
Nevertheless, some environmentally friendly measures have already been implemented to address these concerns. Telemedicine programs have emerged as a promising solution, not only improving access to medical care but also, in many cases, offering potential environmental benefits by reducing patient transportation7-8. The advent of the COVID-19 pandemic further accelerated the adoption of these types of services, and the number of teleconsultations increased tremendously, providing indirect environmental health benefits9-10.
In the province of La Pampa, Argentina, the Ojo Pampa tele-screening program was introduced in 2019 to facilitate early detection of diabetic retinopathy. This program successfully enhanced access to eye examinations by 39%11. However, the environmental impact associated with the implementation of this program remains largely unexplored.
The primary objective of this study was to evaluate the carbon footprint of the tele-screening program for diabetic retinopathy in La Pampa. By assessing the environmental implications of this program, valuable insights can be gained to inform sustainable healthcare practices and contribute to the growing body of knowledge at the intersection of environmental sustainability and public health.

Materials and methods
The Ojo Pampa program was launched in 2019. A retinal camera was transported to 60 rural communities in La Pampa where there were no ophthalmology specialists. Color retinal photographs were taken to diabetic patients and classified asynchronously as “referable” or “non-referable”12. Referable cases were referred for face-to-face consultation. In 2020, the program underwent a change that continues to these days: an ophthalmologist travels to assess “referable” cases. A retrospective and descriptive study was conducted quantifying emissions in two scenarios: with the hypothetical situation without the program (HS) and with program (WP) functioning.
In the hypothetical HS scenario spanning 2019 to 2021, the study calculates emissions as if every “referable” patient treated had traveled from their locality to the corresponding Ophthalmology Department according to health zones13. General Pico corresponds to Health Zone 2, while other localities, including Santa Rosa, align with Health Zones 1, 3, 4, and 5.
In the case of scenario WP, which incorporates tele-screening improvements over the years, in the initial year of the Program (2019), emissions included a one-time assessment of the official vehicle’s mobility from Santa Rosa to each locality. Patients with positive results traveled 30 days later to the nearest ophthalmology center, adding to the initial emissions. In subsequent years (2020 and 2021), the Program evolved, and the ophthalmologist traveled to each locality for the 30-day review of positive cases, reducing patient mobility. WP emissions in these years considered both the official vehicle and the ophthalmologist’s travels to localities with positive cases. The reduction in emissions resulting from the WP scenario was determined by subtracting WP emissions from HS emissions, indicating the environmental impact reduction.
Utilizing this approach, we estimated the distance traveled from each rural community to the respective Ophthalmology Department (in cases where patients were mobilized) and from Santa Rosa to each rural community (in scenarios involving the mobilization of an ophthalmologist). These distance measurements served as crucial inputs for calculating transportation emissions across different situations. Supplementary Information 1 shows data on distances traveled by the official vehicle and the ophthalmologist from Santa Rosa to each locality, as well as distances from each locality to the corresponding ophthalmology center.
Table 1 presents the total number of localities visited and patients treated within the Ojo Pampa Program for each year. The table also provides a breakdown of localities and patients with positive diagnoses requiring a 30-day follow-up.

Table 1. Number of visited localities and patients treated within the Ojo Pampa Program.

 

2019

2020

2021

Total patients

3660

672

2604

Positive patients

912

154

513

Total localities

63

13

54

Localities with positive cases

59

13

49

The emission estimation methodology employed to calculate transport emissions was a top-down approach of the Intergovernmental Panel on Climate Change (IPCC) Level 1 approach, calculating greenhouse gas emissions by multiplying estimated fuel consumption by predetermined emission factors. For the analysis, basic information on emission factors was taken from the methodological guidelines of the IPCC14. The approach is shown in the equation for greenhouse gas (GHG) emissions from transportation (Equation 1)
E = FC * EF
Where
E = emissions [kg]
FC = fuel consumption [TJ]
EF = emission factor [kg/TJ].
The CO2 emission factor accounts for all carbon from fuel, including carbon emitted as CO, volatile organic compounds, and particulate matter. These emission factors vary widely depending on the type of fuel used (gasoline, diesel, or gas). For CO2 emissions, values were extracted from Table 3.2.115. However, emission rates for CH4 and N2O are highly dependent on the combustion technology and emission control present in vehicles. Consequently, emission factors based on fuel alone, without specifying vehicle technology, are considerably uncertain. Therefore, as a precautionary measure, it is encouraged to use higher emission factors derived from Table 3.2.215. Additionally, global warming potentials of 1, 21, and 310 are considered for CO2, CH4, and N2O, respectively16. Table 2 offers a summary of emission factors for gasoline and diesel vehicles.

Table 2. Emission factors by fuel type and emitted gas.

 

EF (Kg/TJ)

 

CO2

CH4

N2O

Gasoline

73.000

86

24

Diesel

74.800

9,5

12

EF: emission factors. CO2: carbon dioxide. CH4: methane. N2O: nitrous oxide.

Table 3. Absolute emissions (Tn) and by gas type for the period 2019-2021.

 

HS

WP

AE (Tn)

2019

2020

2021

2019

2020

2021

CO2

205,16

26,02

151,33

58,01

1,41

9,17

CH4

0,24

0,03

0,18

0,0618

0,0008

0,0048

N2O

0,07

0,01

0,05

0,0180

0,0003

0,0021

Total emissions

231,15

29,32

170,49

64,89

1,52

9,91

Tn: tons. AE: absolute emissions. HS: hypothetical situation. WP: with program.

Table 4. Emissions per treated patient and by gas type for the period 2019-2021 in HS and WP scenarios.

 

HS

WP

EpTP (Kg/cap)

2019

2020

2021

2019

2020

2021

CO2

56,055

38,725

58,113

15,849

2,098

3,523

CH4

0,066

0,046

0,068

0,017

0,001

0,002

N2O

0,018

0,013

0,019

0,005

0,000

0,001

Total emissions

63,155

43,629

65,474

17,730

2,269

3,806

HS: hypothetical situation. WP: with program. EpTP: emissions per treated patient. CO2: carbon dioxide. CH4: methane. N2O: nitrous oxide.

 

Various assumptions were made for the analysis, including vehicle types, catalytic converters, average fuel consumption, individual patient travel, and the destination of patient travel: 1) an average fuel consumption value of 9.1L/100km was estimated based on the highway consumption at 120 km/h of the 70 best-selling gasoline vehicles in Argentina17; 2) the official vehicle is a diesel pickup truck with a consumption of 12 liters per 100 km; 3) the ophthalmologist drove a gasoline vehicle with oxidation catalyst in each city, with and an average consumption of 8.5 L/100km.
As a secondary analysis, emissions per La Pampa resident caused by surface transportation were compared to the emissions reduction per treated patient achieved by the Program. For this purpose, total provincial emissions from surface transportation, without distinction by type, were divided by the estimated population of La Pampa according to the 2022 census18.
To compare the amount of emission reduction per patient in each year, a Mann-Whitney U test was performed. STATA 16.0 software was used for statistical calculation, and a p-value <0.05 was considered statistically significant.
This study was conducted in full compliance with the Declaration of Helsinki.

Results
Absolute emissions
In 2019, the program screened 3,660 patients, with 912 qualifying for referral. In 2020, 672 patients were screened, and 154 were eligible for referral. In 2021, 2,604 patients were screened, and 513 were found to be eligible for referral.
Table 3 presents all emissions in the hypothetical HS scenario and those effectively generated in the WP scenario. CO2 is the predominant GHG, constituting 89% of total emissions. In both situations, it is evident that total emissions with the Program in operation were lower (Fig. 1). As absolute values, the greater differences between years within the same situation are attributed to variations in the number of patients treated and localities visited. Nonetheless, between the HS and WP scenarios, total emissions decreased by 72%, 95%, and 94% for the years 2019, 2020, and 2021, respectively. This underscores the substantial impact of the improvements implemented in the Program over the last two analyzed years.

Emissions per treated patient
This section delves into a detailed analysis of emissions per treated patient, measured in kilograms per capita, and categorizes these emissions by gas type for the years 2019-2021. The comparison between the hypothetical HS and actual WP scenarios provides insights into the program’s impact on individual-level emissions.
Table 4 and figure 2 present a comprehensive breakdown of emissions per treated patient in both scenarios. The data underscores the efficiency of the Ojo Pampa Program in minimizing the carbon footprint associated with each patient. Additionally, the categorization by gas type sheds light on the specific gases affected by the program’s implementation. The differences are less pronounced compared to the analysis of absolute emissions. These differences are more closely tied to the efficiency of the WP scenario—specifically, the number of individuals treated per locality visited—and the HS scenario, reflecting the distance of various localities from the corresponding ophthalmology center.

Emission reduction by the Ojo Pampa program
Emissions per patient were 63 kg without the program, 18 kg with the program, and 4 kg with the program changes. The reduction in emissions per patient was 45 kg, 41 kg, and 62 kg for 2019, 2020, and 2021, respectively (p=0.001). The absolute reduction in eqCO2 emissions for the entire program in 2019, 2020, and 2021 was 166Tn, 28Tn, and 161Tn, respectively. Table 5 and figure 3 show the absolute reductions and reductions per patient achieved during the development of the Ojo Pampa program. The largest absolute savings were achieved in the years when a larger number of patients were served, and a larger number of cities were visited.
Each resident of La Pampa emits 5 kg/day. The program reduced emissions by an average of 49.5 kg over the three years. The emissions avoided by the program are equivalent to 3.6% of the emissions from land transport of La Pampa inhabitants per year, with reference to the data of this category from the subnational disaggregation for La Pampa of the National Inventory of greenhouse gases, reported in the fourth Biennial Update Report (BUR4) of Argentina19. With the program improvements in 2021, the emissions generated by an average La Pampa resident per day in this emissions category were reduced by a factor of six.

Table 5. Absolute reductions and reductions per patient.

 

Absolute emissions (Tn)

Emissions per patient (Kg)

 

2019

2020

2021

2019

2020

2021

CO2

147,15

24,61

142,15

40,20

36,62

54,59

CH4

0,18

0,03

0,17

0,04

0,04

0,06

N2O

0,05

0,01

0,05

0,01

0,01

0,01

Total eq CO2

166,25

27,79

169,58

45,42

41,36

61,66

Tn: tons. Kg: kilograms. CO2: carbon dioxide. CH4: methane. N2O: nitrous oxide. eq CO2: carbon dioxide equivalent.

Discussion
The emissions reduction achieved are of paramount importance in terms of sustainable policies. Such actions are in line with the suggestions made in the editorials of scientific journals after the United Nations expressed its concern about the 1.5°C increase in global warming in September 202120. Therefore, health systems must take action to limit global warming, restore biodiversity, and protect health20.
With the implementation of the Ojo Pampa program, we observed significant reductions in emission per patient: 45 kg in 2019, 41 kg in 2020, and 62 kg in 2021. The notable increase in emission reduction in 2021 can be attributed to key program enhancements, including the introduction of in-person assessments by ophthalmologists in various localities. This strategic change was implemented to ensure that patients requiring direct ophthalmological examination could receive care without the need to travel long distances. By bringing specialized care closer to the patients, we not only improved access to essential eye care, especially for those who faced difficulties in traveling, but also further mitigated overall emissions. The estimated emissions from a La Pampa resident traveling for an eye examination typically amount to 63 kg, considering vehicle emissions alone.
During the pandemic, the program had to adapt to biosafety requirements, leading to a temporary reduction in the frequency of visits. Despite these challenges, the program successfully continued to provide patient care, demonstrating resilience and adaptability in the face of unprecedented global health challenges. These adaptations ensured continued patient care while maintaining a focus on reducing environmental impact, highlighting the program’s commitment to both healthcare excellence and sustainability.
Our study aligns with the growing body of research examining the environmental impact of telemedicine and healthcare activities. Several studies have explored the carbon footprint associated with telemedicine screening programs, providing valuable context for our findings. As in Ojo Pampa, various actions are being taken in the health sector worldwide to reduce pollution. Teleconsultations can be effective in improving environmental sustainability in health care by enabling remote communication and collaboration between sustainability experts and health care professionals10. The use of telemedicine has been found to reduce 0.70 to 372 kg eqCO2 per consultation21. Rodler et al. found that a total of 48 studies met the inclusion criteria, covering 68,465,481 telemedicine consultations and savings of 691,825 tons of CO2 emissions and 3,318,464,047 km of travel distance22. On the other hand, Ravindrane and Patel found that all studies consistently show that telemedicine offers environmental benefits by reducing greenhouse gas emissions associated with travel for medical consultations23. Moreover, three of the studies consider the overall environmental impact, including emissions from telemedicine equipment, and still find telemedicine to be a more environmentally friendly option than traditional face-to-face consultations. A study at Stanford Health Care found a 36% decrease in greenhouse gas emissions from clinic visits between 2019 and 2021, attributed to the increased use of telemedicine services, which helped avoid around 17,000 metric tons of GHGs in 202124.
Additionally, exploring the realm of ophthalmic surgery and carbon-saving activities contributes depth to our discussion. The carbon footprint of a single patient undergoing first cataract surgery is estimated to be 181.8 kg eqCO225. However, reported results vary considerably by center or technique used26-29. To reduce the carbon footprint per surgery, surgical kits could be reused and redesigned, disposable equipment could be reprocessed, two adjacent operating rooms could be used simultaneously, and the nonoperative tasks of the physician could be minimized. It has even been suggested that both eyes could be operated on the same day26,29. While our focus is on telemedicine screening, understanding the broader healthcare landscape’s environmental impact provides a comprehensive perspective.
The limitations of this study were that we do not have accurate data on CO2 generation in the situation without the program. Therefore, we had to assume that all vehicles were gasoline-powered and had oxidation catalysts; each diagnosed patient, when required to travel to the city for the study, did so individually and in his or her private vehicle (not using public transportation); the patient’s final destination was the health center where the study was conducted; and in 2019, all referral-eligible patients traveled to the eye care center on which they depended (Santa Rosa or General Pico) within 30 days for their examination.
This study evaluated the carbon footprint of the Ojo Pampa tele-screening program for diabetic retinopathy in the province of La Pampa, Argentina. The findings provide valuable insights into the environmental implications of implementing such a program and highlight the potential for sustainable healthcare practices at the intersection of environmental sustainability and public health. The results demonstrated significant reductions in emissions per patient associated with the program compared to the hypothetical scenario of patients traveling to the corresponding Ophthalmology Department. The total emissions reduction for the entire program was substantial, contributing to the provincial efforts to mitigate climate change.
Furthermore, the findings also underscored the role of the healthcare sector in minimizing its carbon footprint. By implementing environmentally friendly measures, such as telemedicine, healthcare systems can contribute to global efforts to reduce greenhouse gas emissions. It is essential for health systems to recognize the significance of sustainable policies in addressing the challenges posed by global warming and protecting public health. Actions that limit global warming and reduce pollution are crucial for the well-being of current and future generations. The Ojo Pampa program serves as an example of the positive impact that can be achieved through sustainable healthcare practices, and it provides a foundation for further research and initiatives in this field.


References
1. Woodward AJ, Samet JM. Climate change, hurricanes, and health. Am J Public Health 2018; 108: 33-35.
2. United Nations Framework Convention on Climate Change. Adoption of the Paris agreement.  2015 [online], 2015 (FCCC/CP/2015/L.9/Rev.1). Available in: https://unfccc.int/resource/docs/2015/cop21/eng/l09r01.pdf
3. Karliner J, Slotterback S, Boyd R et al. Health care’s climate footprint: how the health sector contributes to the global climate crisis and opportunities for action. Eur J Public Health 2020; 30 Suppl 5: ckaa165.843.
4. Pichler PP, Jaccard IS, Weisz U, Weisz H. International comparison of health care carbon footprints. Environ Res Lett 2019; 14:064004.
5. Zikhathile T, Atagana H, Bwapwa J, Sawtell D. A Review of the impact that healthcare risk waste treatment technologies have on the environment. Int J Environ Res Public Health 2022; 19: 11967.
6. Morcillo Serra C, Aroca Tanarro A, Cummings CM et al. Impact on the reduction of CO2 emissions due to the use of telemedicine. Sci Rep 2022; 12: 12507.
7. Moncho-Santoja M, Aparisi-Navarro S, Defez García B et al. Health care in rural areas: proposal of a new telemedicine program assisted from the reference health centers, for a sustainable digitization and its contribution to the carbon footprint reduction. Heliyon 2022; 8: e09812.
8. Filfilan A, Anract J, Chartier-Kastler E et al. Positive environmental impact of remote teleconsultation in urology during the COVID-19 pandemic in a highly populated area. Prog Urol 2021; 31: 1133-1138.
9. Blenkinsop S, Foley A, Schneider N et al. Carbon emission savings and short-term health care impacts from telemedicine: an evaluation in epilepsy. Epilepsia 2021; 62: 2732-2740.
10. Pickard Strange M, Booth A, Akiki M et al. The role of virtual consulting in developing environmentally sustainable health care: systematic literature review. J Med Internet Res 2023; 25: e44823.
11. Ortiz-Basso T, Gómez PV, Boffelli A, Paladini A. Evaluación de un programa de teleoftalmología para prevención de la ceguera por diabetes en una zona rural de la Argentina [Assessment of a teleophthalmology program for the prevention of diabetes blindness in a rural area of Argentina]. Rev Fac Cien Med Univ Nac Cordoba 2022; 79: 10-14.
12. Ortiz-Basso T, Boietti BR, Gómez PV et al. Prevalencia de retinopatía diabética en una zona rural de Argentina [Prevalence of diabetic retinopathy in a rural area of Argentina]. Medicina (B Aires) 2022; 82: 99-103.
13. Olivares JL, Belmonte V, Eppler G et al. Niveles de vitamina D en pacientes asistidos en centros de salud pública de la provincia de La Pampa (Argentina). Rev Argent Endocrinol Metab 2019; 56: 41-50.
14. Core Writing Team, Pachauri RK, Reisinger A. Climate change 2007: synthesis report. Geneva: Intergovernmental Panel on Climate Change, 2008. Available in: https://www.ipcc.ch/site/assets/uploads/2018/02/ar4_syr_full_report.pdf
15. Waldron CD. Mobile combustion. In:Eggleston S, Buendia L, Miwa K et al. (eds.). 2006 IPCC Guidelines for national greenhouse gas inventories. Hayama, Japan: By Institute for Global Environmental Strategies for Intergovernmental Panel on Climate Change (IPCC), 2006, vol. 2, chapter 3. Available in: https://www.ipcc-nggip.iges.or.jp/public/2006gl/pdf/2_Volume2/V2_3_Ch3_Mobile_Combustion.pdf
16. Intergovernmental Panel on Climate Change (IPCC). Climate change 1995: the science of climate change: contribution of Working Group I to the Second Assessment Report (SAR). Geneva: IPCC, 1995. Available in:
https://www.ipcc.ch/site/assets/uploads/2018/02/ipcc_sar_wg_I_full_report.pdf
17. Calaza H. Los autos que más y menos consumen en Argentina. In: Autocosmos [web site], April 9th, 2020. Available in: https://noticias.autocosmos.com.ar/2020/04/09/los-autos-que-mas-y-menos-consumen-en-argentina.
18. Instituto Nacional de Estadística y Censos (INDEC) (Buenos Aires). Censo nacional de población, hogares y viviendas 2022: resultados provisionales. 1ª ed. Buenos Aires: INDEC, 2023. Available in: https://www.indec.gob.ar/ftp/cuadros/poblacion/cnphv2022_resultados_provisionales.pdf
19. Argentina. Ministerio de Ambiente y Desarrollo Sostenible (MayDS). Cuarto informe bienal de actualización de Argentina a la Convención Marco de las Naciones Unidas para el Cambio Climático (CMNUCC). Buenos Aires, 2021.
20. Atwoli L, H Baqui A, Benfield T et al. Call for emergency action to limit global temperature increases, restore biodiversity and protect health. Br J Ophthalmol 2021; 105: e2.
21. Purohit A, Smith J, Hibble A. Does telemedicine reduce the carbon footprint of healthcare? a systematic review. Future Healthc J 2021; 8: e85-e91.
22. Rodler S, Ramacciotti LS, Maas M et al GE. The impact of telemedicine in reducing the carbon footprint in health care: a systematic review and cumulative analysis of 68 million clinical consultations. Eur Urol Focus 2023; 9: 873-887.
23. Ravindrane R, Patel J. The environmental impacts of telemedicine in place of face-to-face patient care: a systematic review. Future Healthc J 2022; 9: 28-33.
24. Thiel CL, Mehta N, Sejo CS et al. Telemedicine and the environment: life cycle environmental emissions from in-person and virtual clinic visits. NPJ Digit Med 2023; 6: 87.
25. Morris DS, Wright T, Somner JEA, Connor A. The carbon footprint of cataract surgery. Eye (Lond) 2013; 27: 495-501.
26. Thiel CL, Schehlein E, Ravilla T et al. Cataract surgery and environmental sustainability: waste and lifecycle assessment of phacoemulsification at a private healthcare facility. J Cataract Refract Surg 2017; 43: 1391-1398.
27. Ferrero A, Thouvenin R, Hoogewoud F et al. The carbon footprint of cataract surgery in a French university hospital. J Fr Ophtalmol 2022; 45: 57-64.
28. Latta M, Shaw C, Gale J. The carbon footprint of cataract surgery in Wellington. N Z Med J 2021; 134: 13-21.
29. Goel H, Wemyss TA, Harris T et al. Improving productivity, costs and environmental impact in International Eye Health Services: using the ‘eyefficiency’ cataract surgical services auditing tool to assess the value of cataract surgical services. BMJ Open Ophthalmol 2021; 6: e000642.


Supplementary information 1. Kilometers traveled from each rural community to the corresponding Ophthalmology Department.

Locality / City / Rural community

Corresponding Sanitary Zone

Distances to Santa Rosa (Km)

Distance to the corresponding Ophthalmological Department (Km)

Treated patient in 2019

Treated patient in 2020

Treated patient in 2021

25 de Mayo

Santa Rosa

411

411

140

0

127

Abramo

Santa Rosa

162

162

12

0

15

Algarrobo del Aguila

Santa Rosa

317

317

19

0

21

Alpachiri

Santa Rosa

135

135

46

0

28

Alta Italia

General Pico

161

64

33

0

30

Anguil

Santa Rosa

29

29

42

84

64

Arata

General Pico

117

58

34

0

29

Ataliva Roca

Santa Rosa

47

47

16

0

22

Bernardo Larroude

General Pico

222

83

78

0

43

Bernasconi

Santa Rosa

167

167

57

0

56

Colonia Santa María

Santa Rosa

111

111

10

0

16

Caleufu

General Pico

139

80

25

0

39

Casa de Piedra

Santa Rosa

370

370

0

0

2

Carro Quemado

Santa Rosa

132

132

7

9

0

Catrilo

Santa Rosa

85

85

128

0

71

Ceballos

General Pico

197

67

16

0

0

Chacharramendi

Santa Rosa

203

203

11

0

8

Coronel Hilario Lagos

General Pico

210

80

11

0

0

Colonia Baron

General Pico

84

78

98

88

0

Conhello

General Pico

215

90

45

0

51

Doblas

Santa Rosa

83

83

58

0

56

Dorila

General Pico

148

15

6

0

27

Eduardo Castex

General Pico

82

59

171

0

126

Embajador Martini

General Pico

140

82

1

0

26

Gobernador Duval

Santa Rosa

352

352

10

0

8

General Acha

Santa Rosa

106

106

158

0

218

General Campos

Santa Rosa

158

158

25

0

12

General San Martin

Santa Rosa

182

182

88

0

80

Guatrache

Santa Rosa

184

184

124

0

79

Ingeniero Luiggi

General Pico

156

98

134

0

69

Intendente Alvear

General Pico

198

58

295

0

98

Jacinto Arauz

Santa Rosa

201

201

133

0

77

La Adela

Santa Rosa

276

276

61

0

49

La Gloria

Santa Rosa

53

53

38

0

0

La Humada

Santa Rosa

396

396

40

0

39

La Maruja

General Pico

174

115

28

0

35

La Reforma

Santa Rosa

259

259

6

0

8

Lonquimay

Santa Rosa

66

66

81

89

79

Loventue

Santa Rosa

144

144

3

0

0

Luan Toro

Santa Rosa

125

125

32

34

0

Macachín

Santa Rosa

110

110

87

0

108

Mauricio Mayer

General Pico

77

80

18

15

1

Metileo

General Pico

115

22

26

0

24

Miguel Cane

General Pico

114

63

18

33

0

Miguel Riglos

Santa Rosa

79

79

63

53

0

Monte Nievas

General Pico

93

44

30

0

31

Parera

General Pico

183

123

58

0

42

Pichi Huinca

General Pico

156

97

0

0

11

Puelches

Santa Rosa

262

262

18

0

14

Puelen

Santa Rosa

432

432

22

0

20

Quehue

Santa Rosa

77

77

11

0

10

Quemu Quemu

General Pico

129

49

127

80

90

Rancul

General Pico

211

134

140

0

78

Realico

General Pico

179

91

172

0

85

Rolon

Santa Rosa

138

138

17

0

17

Santa Isabel

Santa Rosa

190

190

62

0

76

Santa Teresa

Santa Rosa

183

183

0

0

15

Speluzzi

General Pico

154

15

8

0

11

Telen

Santa Rosa

158

158

52

43

0

Toay

Santa Rosa

11

11

84

0

105

Trenel

General Pico

122

35

74

0

42

Uriburu

Santa Rosa

45

45

44

19

47

Vertiz

General Pico

171

31

21

0

26

Victorica

Santa Rosa

151

151

128

100

0

Villa Mirasol

General Pico

90

61

23

25

0

Winifreda

General Pico

49

96

37

0

43