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Evaluación de impacto ambiental de las tecnologías sanitarias: estado del arte y perspectivas de futuro<= /p>

Environmental Impact Assessment of health technologies: State of the art and prospects

= ¹⁼	Myrian Alicia Moyón Moyón	<= /span>	https://orcid.org/0000-0003-2714-0831
<= /span>	Distrito 05D01, Ministerio de Salud Pública, Latacunga, Ecuador.= myrian.moyon@05d01.mspz3.gob.ec=
²	Marcelo Isaías Martínez Pilco<= o:p>		https://orcid.org/0009-0006-53= 37-0576
=	Ingeniería Industrial, Facultad de Ingeniería, Universidad Nacional de Chimborazo, Riobamba, Ecuador. marceloimartinez@unach.edu.ec<= /span> <= /o:p>
³	Wendy Michelle Merino Hurtado<= o:p>		https://orcid.org/0009-0002-00= 43-9796
<= /span>	Ingeniería Industr= ial, Facultad de Ingeniería, Universidad Nacional de Chimborazo, Riobamba, Ecuador. wendy.merino@unach.edu.ec <= /o:p>
⁴	Adriana Alejandra Samaniego Vizcaíno		https://orcid.org/0009-0008-85= 13-736X
<= /span>	Ingeniería Industr= ial, Facultad de Ingeniería, Universidad Nacional de Chimborazo, Riobamba, Ecuador. adriana.samaniego@unach.edu.ec= <= /o:p>

	Artículo de Investigación Científica y Tecnológi= ca Enviado: 17/12/2023 Revisado: 20/01/2024 Aceptado: 09/02/2024 Publicado:15/04/2024 DOI: https://doi.org/10.33262/concienciadigi= tal.v7i2.2992

&= nbsp; Cítese:		&= nbsp; Moyón Moyón , M. A., Martínez Pilco, M. I., Merino Hurtado, W. M., & Samani= ego Vizcaíno, A. A. (2024). Evaluación de impacto ambiental de las tecnologías sanitarias: estado del arte y perspectivas de futuro. ConcienciaDigital, 7(2), 108-125. https://doi.org/10.33262/concienciadigital.v7i2.2992<= /span>
	&= nbsp;	CONCIE= NCIA DIGITAL, es una revista multidisciplinar, trimestral, que se publicará en soporte electrónico tiene como misión contribu= ir a la formación de profesionales competentes con visión humaníst= ica y crítica que sean capaces de exponer sus resultados investigativos y científicos en la misma medida que se promueva mediante su intervención cambios positivos en la sociedad. https://concienciadigital.org= La rev= ista es editada por la Editorial Ciencia Digital (Editorial de prestigio registrada en la Cámara Ecuatoriana de Libro con No de Afiliación 663) <= span style=3D'font-size:8.0pt;line-height:115%;font-family:"Times New Roman",s= erif; mso-fareast-font-family:"Times New Roman";color:#0563C1'>www.celibro.org.= ec<= /o:p> <= span style=3D'text-decoration:none'>
	&= nbsp;	Esta r= evista está protegida bajo una licencia Creative Commons AttributionNonCommercialNoDerivatives 4.0 International. Copia de la licencia: http://creativec= ommons.org/licenses/by-nc-nd/4.0/<= /o:p>
Palabras claves: tecnologías, sanitarias, impacto, ambiental, basura, dióxido, carbono.		Resumen = Introdu= cción: El impacto ambiental generado desde el sector sanitario en la actualidad se ha constituido como uno de los principales inconvenientes a nivel mundial, debido entre otras cosas a que las tecnologías sanitarias tuvieron un crecimiento exponencial en cuanto a su elaboración debido a la pandemia del COVID 19 generando niveles de residu= os sólidos sanitarias jamás imaginados; esto incluso obligó a varios gobiern= os de turno a generar políticas sanitarias que traten de mitigar el impacto negativo de estos desechos. Objetivo: La presente investigación ti= ene como objetivo explorar los métodos utilizados en distintas partes del mun= do para evaluar el impacto ambiental generados por las tecnologías sanitaria= s. Metodología: Se realizó una revisión de la literatura científica en las principales ba= ses de datos y se seleccionaron 16 artículos científicos de los últimos cinco ańos que evalúan el impacto ambiental de las tecnologías sanitarias, adem= ás se trabajó mediante un enfoque cualitativo. Resultados: La revisión bibliográfica reflejó que las diversas tecnologías sanitarias tienen una incidencia del 1 al 5% en el impacto ambiental a nivel mundial. Donde la mayor parte de emisiones provienen de inhaladores de que están compuestos= por hidrofluorocarbonos, endodoncia dental, resonancia magnética, laringoscop= ios de metal o plástico, envases farmacéuticos de plástico o aluminio y las pruebas de hematología fueron las tecnologías sanitarias con mayor impacto ambiental. Los principales factores que implican el alto impacto ambiental por parte de las tecnologías sanitarias fueron: uso de electricidad, cons= umo de combustibles fósiles, ropa médica, desinfecciones prolongadas, equipos tecnológicos, reactivos, entre otros. Conclusión: Se concluyó que = la tecnología sanitaria genera a nivel mundial un gran dańo negativo al medio ambiente, donde ańo tras ańo se incrementan los niveles de basura y emisi= ones de dióxido de carbono como principales contaminantes.
Keywor= ds: Technologies, health, impact, environmen= tal, garbage, dioxide, carbon.= <= /o:p>	&= nbsp;	Abstract= <= /o:p> Introduction: The environmental impact generated by the health sector has currently become one of the main drawbacks worldwide, due among other things to the fact that health technologies had exponential growth = in terms of their development due to the COVID pandemic. 19 generating level= s of solid health waste never imagined; this even forced several governments in power to generate health policies that try to mitigate the negative impac= t of this waste. Objective: The objective of this research is to explore the methods used in various parts of the world to evaluate the environmen= tal impact generated by health technologies. Methodology: A review of the scientific literature was conducted in the main databases and 16 scientif= ic articles from the last five years that evaluate the environmental impact = of health technologies were selected. In addition, work was conducted using a qualitative approach. Results: The bibliographic review reflected = that the various health technologies have an impact of 1 to 5% on the environmental impact worldwide. Where most emissions come from inhalers t= hat are composed of hydrofluorocarbons, dental endodontics, magnetic resonance imaging, metal or plastic laryngoscopes, plastic or aluminum pharmaceutic= al containers, and hematology tests were the health technologies with the greatest environmental impact. The main factors that imply the high environmental impact of health technologies were use of electricity, consumption of fossil fuels, medical clothing, prolonged disinfections, technological equipment, reagents, among others. Conclusion: It was concluded that health technology generates great negative damage to the environment worldwide, where year after year the levels of garbage and ca= rbon dioxide emissions as the main pollutants increase.

Introducción

Las tecnologías sanitarias también conocidas como tecnologías de la salud o méd= icas corresponden a herramientas, equipos, dispositivos, procedimientos y sistem= as diseńados que promueven la mejora de la prestación de servicios y atención médica (Sanni et al., 2019). Se relacionan con varias áreas de la medicina, dentro de las cuales se encuentran: medicina, la enfermería, la odontología= , la farmacia, la rehabilitación, la salud pública y la gestión de la salud (Avi= vit & Itamar, 2017). La Organización Panamericana de la Salud (OPS, 2023), menciona que este tipo de tecnologías involucran también los medicamentos y= las técnicas médicas tanto para le prevención como la promoción de la salud.

Existen múltiples tecnologías sanitarias usadas en el Ecuador, sin embargo, las principales se describen a continuación en la siguiente tabla: <= /span>

Tabla 1

Tecnologías sanitarias usadas en el Ecuador=

Tecnología sanitaria	Descripción
Resonancia magnética<= o:p>	Emplea campos magnéti= cos y ondas para crear imágenes del cuerpo, e identificar lesiones en tejidos blandos, problemas neurológicos, enfermedades cardíacas y trastornos musculoesqueléticos.
Implantes auditivos	Estos dispositivos son implantados quirúrgicamente para proporcionar audición a personas con pér= dida auditiva grave o profunda.
Bombas de infusión	Estos dispositivos so= n utilizados para administrar medicamentos, nutrientes o fluidos en el cuerpo de manera controlada y precisa.
Terapia de radiación<= o:p>	La radioterapia utili= za radiación ionizante para destruir células cancerosas y reducir tumores
Prótesis avanzadas	Las prótesis modernas utilizan tecnología avanzada para replicar la función de partes del cuerpo perdidas, como extremidades y órganos.

Fuente: Avivit & Itamar (2017)

Por ello, estas tecnologías principalmente los dispositivos médicos y fármacos tienden a generar un gran dańo para el medio ambiente, donde ańo tras ańo se incrementan los niveles de basura y emisiones de dióxido de carbono como principales contaminantes (Scott et al., 2020). En el Ecuador, este tipo de tecnologías son evaluadas constantemente en base a las sugerencias de la OM= S, sin embargo, a nivel ambiental existen muy pocos estudios (Ministerio de Sa= lud Pública, 2021).

Es muy importante, que de manera constante se evalúe el impacto ambiental con = el fin de identificar cuáles son las tecnologías sanitarias causantes de un da= ńo (Sanni et al., 2019; Scott et al., 2020). Este tipo de impacto toma en consideraci= ón actividades del ser humano y natural y miden sus efectos en el ecosistema, biodiversidad, recursos naturales y clima. Puede generar efectos positivos y negativos y se manifiestan de las siguientes formas: contaminación del aire, agua y suelo, la degradación de los ecosistemas, la pérdida de biodiversida= d, el agotamiento de recursos naturales, el cambio climático, entre otros (Hab= ert et al., 2020).

De esta manera, los dispositivos médicos presentan un impacto ambiental negati= vo ya que son los principales contaminantes del aire, mientras que, los fármac= os contaminan el agua y suelo si no se tiene un adecuado proceso de producción= y desecho (Scherhaufer et al., 2018). La contaminación del aire se debe a la excesiva producción de gases de efecto invernadero, lo cual provocó un calentamiento global en la tierra (Rahman et al., 2022).

Generalmente, se emplea = las evaluaciones del impacto ambiental (EIA), que abarca una serie de herramien= tas utilizadas para evaluar los posibles efectos ambientales de proyectos, políticas, programas o actividades humanas antes de su implementación, con = el fin de identificar medidas de mitigación y tomar decisiones informadas sobre su viabilidad y sostenibilidad ambiental (Dos Santos et al., 2019). Por lo antes seńalado se puede identifi= car de forma clara la utilidad de las EIA en el campo de las tecnologías sanitaria= s, en términos de viabilidad hay que tener en cuenta que todo proceso de remediación debe contemplar un costo apropiado, para que justamente las med= idas planteadas sean ejecutadas.

Cabe recalcar que las evaluaciones del impacto ambiental (EIA) brindan una minuc= iosa información de la geología, hidrología, flora y fauna de un determinado lug= ar, con el fin de identificar algunas consecuencias de una actividad humana y p= or ende el establecimiento de medidas preventivas y de control, para minimizar= al máximo la afectación al medio ambiente (Marchvsky et al., 2018). Como es evidente las evaluaciones son la base para proponer medidas que busque la mitigación del dańo provocado al medio ambiente, pues sin estos datos no se podría plantear medidas que contribuyan de manera sustancial a disminuir los efectos de las tecnologías sanitarias, en donde como se ha podido evidenciar los impactos son negativos y su procesamiento es urgente en algunos países.=

Metodología

El presente estudio tiene un enfoque de investigación cualitativo, el tipo de investigación es investigación bibliográfica-documental, descriptiva, explicativa, además el método de investigación es analítico-sintético, por = lo antes seńalado podemos establecer que se realizó una revisión bibliográfica completa, en donde se establecieron los siguientes criterios:

Criterios de inclusión

·&nb= sp; Artículos de las bases científicas: PubMed, Scielo, Redalyc, MDPI, NCBI y S= cience Direct.

·&nb= sp; Artículos publicados a partir del ańo 2018-2023.

·&nb= sp; Artículos en inglés o espańol.

·&nb= sp; Tipos de estudio: revisiones sistemáticas, ensayos controlados experimentales, estudios de cohorte y meta análisis.

Criterios de exclusión

Artículos de otras bases científicas no establecidas.
Documentos de pregr= ado, posgrado, o doctorado
Artículos con acces= os restringido
Estudios con datos incompletos o en ejecución

Estrategia de búsqueda y presentación de resultados

En primer lugar, se ejecutó una búsqueda en las bases de datos: PubMed, Scielo, Redalyc, MDPI, NCBI y Science Direct. Se utilizaron términos clave para la búsqueda como:

“Environmental impact assessment”

“Health technologie= s”

“Medical devices”

“Impact assessment”=

Después de realizar la búsqueda de artículos en las bases de datos, se evaluaron y seleccionaron a través del método prisma; para esto los documentos deben cumplir con ciertos criterios de inclusión y exclusión establecidos previamente. La selección se realizó mediante la comprobación de ítems del método, este proceso consta con un diagrama de flujo que organiza y estruct= ura los estudios con criterios de identificación, cribado, elegibilidad y selección. Tal como se evidencia a continuación en la figura 1: =

Figura <= b>1=

Método PRISMA para la búsqueda de resultados

Fuente: Do Nascimeinto et al. (2019)

Cabe recalcar que existen un número considerable de investigaciones en donde se refleja la preocupación de distintos organismos gubernamentales y privados sobre los impactos negativos que genera la tecnología sanitaria, al punto de ser la responsable de gases de efecto invernadero que se ha constituido un aditamento para el calentamiento global y de una sobre producción después d= e la pandemia, lo que origina grandes cantidades de desechos sólidos que en vari= os países fueron el detonante para generar políticas ambientales.

Resultados

Los resultados de la revisión bibliográfica docume= ntal se presentan en la siguiente tabla, haciendo relación entre la evaluación d= el impacto ambiental y la tecnología sanitaria utilizada de manera frecuente e= n el Ecuador y que ha sido aplicada en el mundo, así podemos recalcar los siguie= ntes:

Tabla 2

Resultados de la revisión bibliográfica-documental

Título

Autores y ańo de publica= ción

Metodología

Tecnología sanitaria

Resultados

La huel= la ambiental de la atención sanitaria: una evaluación global

&n= bsp;

Lenzen = et al. (2020)

Huella = de carbono

Atención sanitaria

La aten= ción sanitaria global tiene un impacto ambiental mundial entre 1-5%. En términos de emisiones de gases de efecto invernadero y contaminantes atmosféricos, el sector sanitario causa una gran proporción de la huella total (4,4% de los gases de efecto invernadero, 2,8% de las PM, 3,4% de l= os NO _y 3,4% de las emisiones de N2O3). ·6% de SO ₂ ).

Impacto ambiental de los inhaladores para enfermedades respiratorias.<= /span>

&n= bsp;

Panigon= e et al. (2020)

Huella = de carbono

Inhalad= ores de dosis medidas e inhaladores de polvo seco

De los inhaladores analizados se determinó que los de dosis media presentan el m= ayor impacto ambiental, ya que en su infraestructura presentan un impulsor. Los resultados de huella de carbono fueron: Inhaladores de dosis media: 82-11= 9 g CO_2,Inhaladores de polvo seco: 8 g CO₂<= /span>

Sosteni= bilidad ambiental en endodoncia. Una evaluación del ciclo de vida (LCA) de un procedimiento de tratamiento de conducto

&n= bsp;

Duane et al. (2020)

Análisi= s de ciclo de vida: ISO 14040:2006

Procedi= miento de endodoncia dental

Una end= odoncia dental aporta 4,9 kg de emisiones de dióxido de carbono equivalente (CO2 = eq), debido a los siguientes factores: ropa dental, desinfección de superficies (isopropanol), el babero desechable (papel y plástico), los instrumentos = de acero inoxidable de un solo uso y el uso de electricidad

Tabla 2

Resultados de la revisión bibliográfica-documental (continuación)

Título<= o:p>

Autores= y ańo de publicación

Metodol= ogía

Tecnolo= gía sanitaria

Resulta= dos

Evaluac= ión del ciclo de vida de envases farmacéuticos

&n= bsp;

Bassani= et al. <= span style=3D'mso-bookmark:_Hlk157785350'>(2022)=

Análisi= s de ciclo de vida

Envases farmacológicos

Existe = una gran variación de impactos dentro de los envases alternativos para un mis= mo medicamento, siendo más significativa para las ampollas (hasta cinco vece= s) que para los frascos y sobres. El uso de aluminio presenta impactos muy altos, particularmente en cuanto a la acidificación, mientras que, el PVC presento impactos ambientales muy bajos.

Contami= nación de la atención médica y dańos a la salud pública en los Estados Unidos: u= na actualización

&n= bsp;

Eckelma= n et al. <= span style=3D'mso-bookmark:_Hlk157785350'>(2020)=

Emision= es de gases efecto invernadero

Atención sanitaria

En el 2= 018 se produjeron más de 500 millones de toneladas métricas, con una producci= ón per cápita de 1700 Kg CO_2.Esto debido a los siguientes factor= es: equipos médicos, suplementos farmacéuticos y químicos, plásticos, textile= s, papel, equipos tecnológicos.

Emision= es ambientales del ciclo de vida y dańos a la salud del sistema de salud can= adiense: un análisis económico-ambiental-epidemiológico

Eckelma= n et al. <= span style=3D'mso-bookmark:_Hlk157785350'>(2018)=

Emision= es de gases efecto invernadero

Atención sanitaria

El sist= ema de salud fue responsable de 33 millones de toneladas de equivalentes de dióxido de carbono (CO ₂ e), así como de más de 200.= 000 toneladas de otros contaminantes. Los medicamentos se consideran como el principal factor que genera dańos en la salud.

Tabla 2

Resultados de la revisión bibliográfica-documental (continuación)

Título<= o:p>

Autores= y ańo de publicación

Metodol= ogía

Tecnolo= gía sanitaria

Resulta= dos

La huel= la de carbono de la atención sanitaria australiana<= /p>
&n= bsp;

Malik et al. (2018)

Emision= es de gases efecto invernadero

Atención sanitaria

Generó emisiones de CO 2 e de alrededor de 35772 kilotones. Siendo los medicamentos farmacéuticos, radiología y patología los principales generadores. Las emisiones directas de CO 2 e provenientes del = uso de combustible (gas para agua caliente) en el cuidado de la salud contribuyeron al 10% de las emisiones totales de CO 2 e, mientr= as que las emisiones indirectas de CO 2 e debidas a las compras a otros sectores económicos contribuyeron a casi el 90 % de las emisiones totales.

La huel= la de carbono del diagnóstico por imágenes hospitalarias en Australia

&n= bsp;

McAlist= er et al. (2022)=

Análisis del ciclo de vida

Radiogr= afía de tórax (CXR), radiografía de tórax móvil (MCXR), tomografía computariza= da (CT), imágenes por resonancia magnética (MRI) y ultrasonido

Las emisiones medias de CO 2 e fueron de 17,5 kg/exploración para resonancia magnética; 9,2 kg/exploración para TC; 0,8 kg/exploración para CXR; 0,5 kg/exploración para MCXR; y 0,5 kg/exploración para ecografía. Los principales factores fueron: tiempo de escaneo y uso excesivo de electricidad.

Evaluac= ión del ciclo de vida y métodos de cálculo de costos para la adquisición de dispositivos: comparación de laringoscopios reutilizables.

Sherman= et al. (2018)=

Evaluac= ión del impacto del ciclo de vida

Laringo= scopios

<= span style=3D'font-size:10.0pt;line-height:115%;font-family:"Times New Roman",= serif; mso-ansi-language:ES-EC'>Se determinó que los mangos y hojas de laringoscopios que en su estructura presentan metal y plástico tuvieron u= na producción entre 16-18 veces más cantidades de dióxido de carbono, a diferencia de los que son de acero reutilizable. Esto debido a que requieren niveles de limpieza adecuados, un reprocesamiento y desgaste prematuro antes de su v= ida útil.

Tabla 2

Resultados de la revisión bibliográfica-documental (continuación)

Título<= o:p>

Autores= y ańo de publicación

Metodol= ogía

Tecnolo= gía sanitaria

Resulta= dos

Impacto= en la huella de carbono de la elección de inhaladores para el asma y la EPOC=

&n= bsp;

Janson = et al. (2019)

Emision= es de gases efecto invernadero

Inhalad= ores

Los inhaladores de dosis medidas (MDI) que contenían clorofluorocarbonos fuer= on reemplazados por inhaladores de polvo seco (DPI) y MDI que contenían hidrofluorocarbonos (HFC). Si bien los HFC no agotan la capa de ozono, generan potentes gases de efecto invernadero. La huella de carbono anual = (CO2 e) fue de 17 kg para MDI; y 439 kg para HFC.

La huel= la de carbono de las pruebas de patología

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

McAlist= er et al. (2020)=

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

Emision= es de gases efecto invernadero

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

Pruebas= de patología

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

Las emisiones de CO ₂ e para las pruebas de hematología fueron de 82 g/prueba, 73 a 91 g/prueba para el perfil de coagulación y de 116 g/prueba para el examen de sangre completo. Las emisiones de CO ₂ e para pruebas bioquímicas fueron de 0,5 g/prue= ba de CO ₂ e 0,4–0,6 g para la proteína C reactiva, 45 = a 53 g/prueba) para la evaluación de gases en sangre arterial, y 99 g/prueba p= ara la evaluación de urea y electrolitos. La mayoría de las emisiones de CO ₂ e estuvieron asociadas con la recolección de muestras, los reactivos de laboratorio y el uso de energía.

Tabla 2

Resultados de la revisión bibliográfica-documental (continuación)

Título<= o:p>

Autores= y ańo de publicación

Metodol= ogía

Tecnolo= gía sanitaria

Resulta= dos

Desafío= s y soluciones para estimar el impacto ambiental en la evaluación de tecnologías sanitar= ias.

&n= bsp;

Hubbert= et al. (2023)

&n= bsp;

Análisi= s de ciclo de vida.

&n= bsp;

ACV hipotético para un bisturí de un solo uso/reutilizable.=

La aten= ción sanitaria tiene un alto coste medioambiental; El NHS es responsable del 4= % al 5% de la huella de carbono del Reino Unido. En consecuencia, el impacto ambiental está ganando importancia en la toma de decisiones en Evaluación= de Tecnologías Sanitarias (ETS), y las Evaluaciones del Ciclo de Vida (ECV) pueden cuantificar este impacto. Sin embargo, existen desafíos actuales e= n la realización de ACV, lo que requiere que los resultados se interpreten con cautela.

Discusión=

En los últimos ańos la evaluación del impa= cto ambiental se ha transformado en una medida para revertir los efectos del ca= mbio climático, y sobre todo de prevención. Es promovido en todo el mundo e incl= uso aceptado por las Naciones Unidas, como una política pública ambiental (Pere= vochtchicova, 2023). Incluso, es una gran herramienta para el logro del desarrollo sosten= ible ya que ayuda de manera rápida la toma de decisiones que no afecten el medio ambiente y generen protección (Do Nascimeinto et al., 2019). Delimita las actividades humanas y naturales que pueden causas un dańo al medio ambiente= en base a (Espinoza, 2021):

Acciones satisfactorias al medio ambiente

Consecuencias positivas o negativas detectadas al inicio

Prevención y mitigación de las consecuencias negativas

Calificación = del cumplimiento con las políticas medioambientales

Ejecución de estudios de prevención para impactos positivos y negativos.

A pesar de la exigencia de ejecutar Evaluaciones de Impacto Ambiental, en el Ecuador se evidencian escasos investigaciones sobre la temática y enfocada únicamente en temas de construcción, sistemas de alcantarillado, cultivos, actividad agrícola, agu= as residuales e incluso actividades turísticas (Ministerio de Salud Pública [M= SP], 2021; Perevochtchicova, 2023). Sin embargo, en referencia a tecnologías sanitarias no existen, motivo por el cual se identificó cuáles son las más empleadas en el país y se dio búsqueda de EIA en los mismos.

Se identificó que a nivel mundial toda tecnología sanitaria tiene un impacto global que oscila entre el 1-5%, debi= do a los siguientes aspectos: uso de recursos naturales, generación de residuos, emisiones contaminantes, entre otros. El sector sanitario es responsable del 4,4% de las emisiones totales de GEI. Esto es significativo, ya que los GEI contribuyen al cambio climático al atrapar el calor en la atmósfera. Entre estos gases, se menciona el N2O, que es un gas de efecto invernadero potent= e, con una contribución del 3,4% por parte del sector sanitario (Lenzen et al., 2020).

A la par a la investigación anterior se encuentras las descritas pro Bassani et al. (2022)= y Eckelman et = al. (2018), mismas que in= dican datos muy preocupantes sobre el impacto ambiental a causa de todo el sector= de la salud. Los cuales indican que a causa de los medicamentos, radiología, patologías y uso de electricidad generan altas cantidades de dióxido de car= bono (200000) y gases de efecto invernadero. Lo cual implica en la necesidad de revisar las prácticas de producción, distribución y eliminación de medicame= ntos para minimizar su impacto negativo en la salud humana y el medio ambiente. = En el 2018 se produjeron más de 500 millones de toneladas métricas, con una producción per cápita de 1700 Kg CO_2.

De igual manera, se encontraron estudios q= ue evalúan el impacto ambiental de ciertas tecnologías sanitarias, tales como: inhaladores, dispositivos patológicos, laringoscopios, exámenes radiológico= s, implementos dentales entre otros. Con respecto a los inhaladores que sirven principalmente para curar el asma se identificó el estudio de Panigone et a= l. (2020) y Janson et al= . (2019), en los cuales analizaron los de dosis medias (MDI) y de Polvo seco (DPI), determinando qu= e el primer tipo son los causantes de un mayor impacto ambiental, con una huella= de carbono que oscila entre 82-119 gCO_2eprincipalmente gracias a la presencia de un impulsor_.Por otra parte, la segunda investigaci= ón delimita que la composición del inhalador genera también altos impactos ambientales, ya que la mayor parte cuentan con hidrofluorocarbonos uno de l= os principales compuestos químicos contaminantes. Lo cual evidencia que la elección del tipo de inhalador puede tener un impacto significativo en el m= edio ambiente.

En cuanto a aspectos dentales, se tomó en consideración un estudio de endodoncias, por parte de Duane et al. (2020). Determinaron = que este procedimiento ocasiona alrededor de 4,9 Kg de dióxido de carbono equivalente (CO2 eq). A causa de una serie de factores, mismas que se descr= iben a continuación:

Ropa dental:<= /span> probablemente hecha de materiales sintéticos como poliéster o polipropileno, puede contribuir a las emisiones de CO2 eq durante su fabricación, transport= e y eliminación al final de su vida útil (Duane et al., 2020). =

Desinfección = de superficies: El uso de isopropanol para la desinfección = de superficies es una práctica común en entornos médicos y odontológicos.= Sin embargo, el isopropanol es un compuesto químico que puede contribuir a= las emisiones de gases de efecto invernadero durante su producción y trans= porte, así como durante su uso y eliminación (Duane et al., 2020).=

Electricidad:= El uso de electricidad durante la endodoncia, por ejemplo, para alimentar equipos médicos y luces, también puede contribuir a las emisiones de CO2 eq, dependiendo de la fuente de energía utilizada para generarla. Si la electricidad proviene de fuentes renovables como la energía solar o eólica, las emisiones asociadas pueden ser menores en comparación con = la electricidad generada a partir de combustibles fósiles (Duane et al., = 2020).

McAlister et al. (2022), analizó el impact= o de exámenes por rayos X, a través de la cual se determinó que la resonancia magnética puede generar hasta 17,5 Kg de CO 2 e, 9,2 Kg para Tomografía computarizada, 0,8 Kg en una radiografía de tórax. Esta variación puede explicarse por las diferencias en la tecnología utilizada, el tiempo = de escaneo y los requisitos de energía asociados con cada tipo de exploración.= El factor principal de esto es el tiempo del examen, donde los procedimientos = que requieren más tiempo de escaneo, como la resonancia magnética y la tomograf= ía computarizada, tienden a generar mayores emisiones de CO2 eq debido al cons= umo prolongado de energía.

Sherman et al. (2018), por su parte identificaron un impacto ambiental alto en los laringoscopios que presentan= en su estructura metal o plástico debido a que todo el proceso de fabricación implica grandes insumos para ser usados muy pocas veces. Bassani et al. (2022), en su investi= gación de envases farmacológicos afirma también que el alto impacto se debe a la presencia de plásticos y aluminios. Mientras que McAlister et al. (2020), en pruebas patológicas determinaron que las altas emisiones de dióxido de carb= ono se deben principalmente a la recolección de muestras, los reactivos de laboratorio y el uso de energía.

Conclusiones<= /b>

·&nb= sp;        Se determinó que las tecnologías sanitarias utiliz= adas de manera frecuente en el Ecuador generan un impacto ambiental negativo, de= bido a que producen grandes cantidades de gases de efecto invernadero, mismos que promueven el cambio climático, afectando incluso a la salud humana. A pesar= de que las tecnologías sanitarias son un componente esencial para garantizar u= na atención médica eficiente, efectiva y de calidad en todos los niveles del sistema de salud, es muy importante que se analice todo el ciclo de vida de estos productos con el fin de prevenir dańos severos al medio ambiente.

·&nb= sp;        Se identificó que toda la atención sanitaria impli= ca un alto impacto ambiental con una incidencia del 1-5% a nivel mundial. Dond= e la mayor parte de emisiones de dióxido de carbono se debe al consumo de combustibles fósiles. De las tecnologías sanitarias analizadas se identificó que las causantes de altos impactos ambientales fueron: inhaladores de dosis medias compuestos por hidrofluorocarbonos, endodoncia dental, resonancia magnética, laringoscopios de metal o plástico, envases farmacéuticos de plástico o aluminio y las pruebas de hematología.

·&nb= sp;        Se determinó que los principales factores que impl= ican el alto impacto ambiental por parte de las tecnologías sanitarias fueron: u= so de electricidad, consumo de combustibles fósiles, ropa médica, desinfeccion= es prolongadas, equipos tecnológicos, reactivos, entre otros, lo que sin duda alguna han promovido la creación y aplicación de políticas ambientales que disminúyanla afectación ambiental por parte de los gobiernos de turno.

·&nb= sp;        Se concluyó que los resultados de las distintas investigaciones resaltan la importancia de evaluar y comparar el impacto ambiental de diferentes tecnologías sanitarias, y de considerar cuidadosame= nte las implicaciones ambientales al elegir entre diferentes opciones de tratamiento, además subrayan la necesidad continua de buscar alternativas m= ás ecológicas y sostenibles en el diseńo y fabricación de dispositivos médicos para minimizar su impacto en el medio ambiente.

Conflicto de intereses

Los autores declaran que no existe conflicto de intereses en relación con el artículo presentado.

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ISSN: 2600-5859

Vol. 7 No. 2, pp. 108 – 125, abril - junio 2024=

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ISSN: 2600-5859

Vol. 7 No. 2, pp. 91 – 107, abril - junio 2024<= /span>

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Título	Autores y ańo de publica= ción	Metodología	Tecnología sanitaria	Resultados
La huel= la ambiental de la atención sanitaria: una evaluación global &n= bsp;	Lenzen = et al. (2020)	Huella = de carbono	Atención sanitaria	La aten= ción sanitaria global tiene un impacto ambiental mundial entre 1-5%. En términos de emisiones de gases de efecto invernadero y contaminantes atmosféricos, el sector sanitario causa una gran proporción de la huella total (4,4% de los gases de efecto invernadero, 2,8% de las PM, 3,4% de l= os NO _y 3,4% de las emisiones de N2O3). ·6% de SO ₂ ).
Impacto ambiental de los inhaladores para enfermedades respiratorias.<= /span> &n= bsp;	Panigon= e et al. (2020)	Huella = de carbono	Inhalad= ores de dosis medidas e inhaladores de polvo seco	De los inhaladores analizados se determinó que los de dosis media presentan el m= ayor impacto ambiental, ya que en su infraestructura presentan un impulsor. Los resultados de huella de carbono fueron: Inhaladores de dosis media: 82-11= 9 g CO_2,Inhaladores de polvo seco: 8 g CO₂<= /span>
Sosteni= bilidad ambiental en endodoncia. Una evaluación del ciclo de vida (LCA) de un procedimiento de tratamiento de conducto &n= bsp;	Duane et al. (2020)	Análisi= s de ciclo de vida: ISO 14040:2006	Procedi= miento de endodoncia dental	Una end= odoncia dental aporta 4,9 kg de emisiones de dióxido de carbono equivalente (CO2 = eq), debido a los siguientes factores: ropa dental, desinfección de superficies (isopropanol), el babero desechable (papel y plástico), los instrumentos = de acero inoxidable de un solo uso y el uso de electricidad

Título<= o:p>	Autores= y ańo de publicación	Metodol= ogía	Tecnolo= gía sanitaria	Resulta= dos
Evaluac= ión del ciclo de vida de envases farmacéuticos &n= bsp;	Bassani= et al. <= span style=3D'mso-bookmark:_Hlk157785350'>(2022)=	Análisi= s de ciclo de vida	Envases farmacológicos	Existe = una gran variación de impactos dentro de los envases alternativos para un mis= mo medicamento, siendo más significativa para las ampollas (hasta cinco vece= s) que para los frascos y sobres. El uso de aluminio presenta impactos muy altos, particularmente en cuanto a la acidificación, mientras que, el PVC presento impactos ambientales muy bajos.
Contami= nación de la atención médica y dańos a la salud pública en los Estados Unidos: u= na actualización &n= bsp;	Eckelma= n et al. <= span style=3D'mso-bookmark:_Hlk157785350'>(2020)=	Emision= es de gases efecto invernadero	Atención sanitaria	En el 2= 018 se produjeron más de 500 millones de toneladas métricas, con una producci= ón per cápita de 1700 Kg CO_2.Esto debido a los siguientes factor= es: equipos médicos, suplementos farmacéuticos y químicos, plásticos, textile= s, papel, equipos tecnológicos.
Emision= es ambientales del ciclo de vida y dańos a la salud del sistema de salud can= adiense: un análisis económico-ambiental-epidemiológico	Eckelma= n et al. <= span style=3D'mso-bookmark:_Hlk157785350'>(2018)=	Emision= es de gases efecto invernadero	Atención sanitaria	El sist= ema de salud fue responsable de 33 millones de toneladas de equivalentes de dióxido de carbono (CO ₂ e), así como de más de 200.= 000 toneladas de otros contaminantes. Los medicamentos se consideran como el principal factor que genera dańos en la salud.