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Generación y segregación de residu= os sólidos domiciliarios durante la cuarentena por Covid-19 en Panamá, estudio= de caso

 

 

Household solid waste generation and sorting during Covid-19 quarantine in Panama, case study

 

Norvin Requena Sanchez1, Dalia Carbonel Ramos2*, & Erick Vallester3

 

1Equipo Técnico de Residu= os Sólidos, Facultad de Ingeniería Ambienta, Universidad Nacional de Ingenierí= a, Perú.

2Equipo Técnico de Residu= os Sólidos, Facultad de Ingeniería Ambienta, Universidad Nacional de Ingenierí= a, Perú.

3= Universidad Tecnológica de Panamá UTP, Panamá.

 

* Autor por correspondencia: Dalia Carbonel Ramos, dc= arbonelr@uni.pe

   Av. Túpac Amaru 210, Rímac, Apartado 1301, Lima, Perú.=

 

 

Recibido: 30 de noviembre de 2020.

 Aceptado: 06 de abril de 2021<= o:p>

=  

 

= Resumen

 

La pandemia del Covid-19 ha provocado la declaratoria de cuarentenas en casi todos los países del mundo, en Panamá se mantuvo un confinamiento estricto entre los meses de marzo y setiembre. A p= esar de la importancia de la gestión de los residuos sólidos en las ciudades la información sobre el impacto de la cuarentena en la generación y composició= n de residuos no ha sido lo suficientemente recopilada y difundida. En este estu= dio se presenta una metodología innovadora para recolectar información sobre los residuos domiciliarios sin salir de casa. Este trabajo muestra los resultad= os de una encuesta cerrada sobre hábitos de generación y segregación de residu= os en seis provincias del país y los datos de caracterización y composición de= los residuos sólidos domiciliarios en tres distritos de la provincia de Panamá.= Los resultados de las encuestas evidencian las deficiencias del servicio de recolección de residuos en diferentes zonas del país. La generación per cáp= ita domiciliaria de la provincia de Panamá es 0.409 kg/hab./día (27% de error y 0.23 de desviación estándar), este valor es menor a otros hallados previame= nte lo que podría deberse a una disminución en la capacidad de compra de las familias ocasionada por el desempleo a raíz de la cuarentena. En la composi= ción de residuos la proporción de residuos orgánicos y peligrosos aumentó. Los residuos orgánicos pueden haber aumentado por una mayor frecuencia y cantid= ad de alimentos preparados en casa. El aumento de residuos peligrosos es un indicador importante para emitir recomendaciones que reduzcan el riesgo del personal de servicio de recolección de residuos.

 

Palabras clave: Generación de residuos, Composición de residuos, Residuos sólidos domiciliarios, Covid-19, Panamá. <= /i>


Abstract

 

The Covid-19 pandemic has caused quarantines in almost all the world countries. In Panama, strict confinement was maintained between March and September. Despite the importance of solid waste management in cities, information on the impact of quarantine on the generation and composition of waste has not been sufficiently collected and disseminated. This study pres= ents a novel methodology to collect information on household waste without leavi= ng the house. This work shows the results of a survey on waste generation and segregation habits in six provinces of the country; and data on household w= aste characterization and composition in three districts in the province of Pana= ma. The survey results show the deficiencies of the waste collection service in different areas of the country. The per capita household generation in Pana= ma's province is 0.409 kg per capita per day (27% error and 0.23 standard deviation). This value is lower than others previously found, which could be due to a decrease in families' purchasing capacity caused by unemployment a= s a result of the quarantine. Regarding waste composition, the proportion of organic and hazardous waste increased. Organic waste may have increased due= to a greater frequency and quantity of food prepared at home. The increase in hazardous waste is an essential indicator for issuing recommendations to re= duce waste collection service personnel's risk.

 

Keywords: Waste generation, Wa= ste composition, Household solid waste, Covid-19, Panama.

 

= Introducción

 

El Covid-19 ha tenido un gran impacto en América Latina. Al momento de escribir este artículo en la región se presentan el 5= 0% de los casos totales en el mundo y el 55% de fallecidos (WHO, 2020). De acuerdo a la Organización Mundial de la Salud los países con mayor número de casos en la región son Brasil, Argentina y Colombia (WHO, 2020). Los primeros casos de esta enfermedad se reportaron en la región el primer trimestre del 2020, a medida que los casos iban en aumento, en la primera quincena de marzo, la mayoría de países decretó cuarentena en diferentes modalidades: focalizada, obligatoria o recomendada (Cheq= uea, 2020). Gran parte de las ciudades de la región mantuv= o un confinamiento estricto hasta el mes de setiembre cuando estas condiciones fueron levantándose poco a poco (Fran= ce24, 2020).

En Panamá el primer caso confirmado de Covid-19 se registró el 9 de marzo. El = 13 de marzo se declaró emergencia nacional, en los días subsiguientes se cerra= ron las fronteras, se suspendieron las actividades recreativas, se estableció el toque de queda y se ordenó el cierre temporal de establecimientos comercial= es y empresas (Minsa, 2020a)<= /span>. Estas condiciones estrictas de cuarentena se mantuvieron durante seis meses= , a partir del 7 de setiembre se inició una reapertura gradual de las actividad= es económicas y desde el 14 de setiembre se eliminaron las restricciones de movilidad ciudadana. A la fecha en Panamá se han registrado 117,300 casos confirmados y 2,448 defunciones (Minsa, 2020b)<= /span>.

Gestión de residuos en América Latina y Panamá

 <= /span>

En América Latina el 50% de los residuos no se reciclan, la ONU calcula que 145.000 t/día se destinan a basurales, quema u o= tras prácticas inadecuadas; esto equivale al 27% de la población regional, o los residuos generados por 170 millones de personas (Savino, Solórz= ano, Quispe, & Correal, 2018).

La gestión de residuos sólidos en Panamá presenta deficiencias en todas sus fases (DefensoríaDelP= ueblo, 2007; Diéguez Pinto, 2018). Solo el 43.1% de los municipios del país cuenta = con un plan de manejo de residuos sólidos (Grau et al., 2015). En el Plan Nacional de Gestión Integral de Residuos Sólidos de Panamá= (Ineco, 2017) se estima que los residuos generados por un 74% de la población termi= nan en rellenos sanitarios; sin embargo, estos datos contrastan con el diagnóst= ico de vertederos de la AAUD (Autoridad de Aseo Urbano y Domiciliario, <= !--[if supportFields]>ADDIN CSL_CITATION {"citationItems":[{"id":"ITEM-1","itemDa= ta":{"author":[{"dropping-particle":"",&= quot;family":"AAUD","given":"","non= -dropping-particle":"","parse-names":false,"s= uffix":""}],"id":"ITEM-1","issued&q= uot;:{"date-parts":[["2015"]]},"number-of-pages&qu= ot;:"155","publisher-place":"Ciudad de Panamá","title":"Diagnóstico de los Vertederos a Niv= el Nacional","type":"report"},"uris":["= ;http://www.mendeley.com/documents/?uuid=3D016791be-99ea-4249-a3e8-a6da65de= fa38"]}],"mendeley":{"formattedCitation":"(AA= UD, 2015)","plainTextFormattedCitation":"(AAUD, 2015)","previouslyFormattedCitation":"(AAUD, 2015)"= ;},"properties":{"noteIndex":0},"schema":&quo= t;https://github.com/citation-style-language/schema/raw/master/csl-citation= .json"}(AAUD, 2015)) donde se constata que gran parte de l= os municipios realizan la disposición final en vertederos a cielo abierto. Esta misma autoridad reporta la existencia de seis rellenos sanitarios en todo el país (AAUD, 2019) para un total de 81 municipios, e incl= uso esta información es debatible pues en la práctica el único relleno sanitari= o es el de Cerro Patacón que en realidad es considerado como un vertedero controlado. Todos estos lugares de disposición final no son manejados adecuadamente y generan graves problemas ambientales y de salud (DefensoríaDelP= ueblo, 2007; Perea, 2019; Rivas, 2015). En temas de reciclaje queda un largo = camino por recorrer, una encuesta realizada a los alcaldes de 89% de los municipio= s de Panamá indica que, de forma general, no se realiza separación de los residu= os (Ineco, 2017).=

 

Cambios en la generación= de residuos en la pandemia en Panamá

 

En el distrito de Panamá, la AAUD informó que en= tre la última semana de marzo y la primera quincena de abril se registró un aum= ento del 25% en la recolección de residuos de los 26 corregimientos del distrito capital (AAUD, 2020a). En el mes de agosto, tras la reapertura de alg= unas actividades comerciales, se observó gran cantidad de mascarillas y guantes usados en diversos puntos (AAUD, 2020b). Además, se reportó que 100 trabajadores de aseo entre personal administrativo y de campo se contagiaron con el Covid-19 (AAUD, 2020b).

Durante la pandemia de Covid-19 no ha habido una suficiente difusión sobre los datos de generación y reciclaje de residuos <= /span>(Naughton, 2020). Esto es aún más evidente en el caso de América Latina donde la carencia de información s= obre gestión de residuos sólidos de la mayor parte de los países de la región es= un aspecto de fundamental importancia (Savino et al.,= 2018). En Panamá, por ejemplo, la informació= n más reciente sobre la generación de residuos se encuentra en el <= span lang=3DES-TRAD style=3D'font-size:10.0pt;font-family:"Times New Roman",seri= f; mso-fareast-font-family:"Palatino Linotype";color:#231F20;letter-spacing:-.= 1pt; mso-ansi-language:ES-TRAD;mso-bidi-font-weight:bold'>Plan Nacional de Gesti= ón Integral de Residuos Sólidos elaborado el 2017 (Ineco, 2017), la data a nivel distrital es escasa.

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= Método

 

Objetivos

 

El presente estudio presenta una metodología novedosa para recopilar información sobre la gestión de residuos sin necesi= dad de un trabajo de campo que aumente el riesgo de exposición. Es importante recolectar este tipo de datos para conocer cómo la pandemia y la cuarentena= han impactado en la generación y composición de los residuos sólidos en las principales ciudades de la región, esta data será muy útil para la toma de decisiones en la gestión de residuos sólidos. En este estudio se presentan = los resultados de hábitos de generación y segregación de residuos, así como dat= os de caracterización y composición de los residuos sólidos de la provincia de Panamá.

 

P<= /span>oblación, Muestra e Instrumento

 

El estudio fue organizado por los alumnos del cu= rso de “Gestión e ingeniería de residuos sólidos” de la Facultad de Ingeniería Ambiental de la Universidad Nacional de Ingeniería de Perú. La metodología = del presente estudio ha sido previamente aplicada en algunas ciudades del Perú y Honduras. Con el objetivo principal de ampliar y difundir tanto la metodolo= gía como los alcances del estudio se contactó al docente y alumnos del curso de “Desechos sólidos” de la carrera de Saneamiento y Ambiente de la Facultad de Ingeniería Civil de la Universidad Tecnológica de Panamá para que participa= ran en el estudio. Este grupo fue la muestra seleccionada, las razones para su selección fueron el conocimiento en temas de gestión de residuos.

Los datos se recopilaron durante la primera sema= na de setiembre del 2020. El estudio consistió en una encuesta cerrada sobre hábitos de generación, número de personas en casa y segregación de residuos= . En ella participaron 47 personas de las provincias de Panamá (30), Panamá Oeste (7), Colón (5), Herrera (2), Chiriquí (2) y Veraguas (1). El 91% de los participantes viven en un área urbana.

Luego se hizo una capacitación en caracterizació= n de residuos el 7 de setiembre, donde se enseñó a clasificar los tipos de resid= uos en orgánicos, inorgánicos aprovechables, no aprovechables y peligrosos. Así mismo en este taller se instruyó a los participantes a comenzar a elaborar = un ecoladrillo, donde en una botella limpia y vacía colocarían residuos de envolturas de golosinas, bolsas de plástico, recibos de caja o cajeros, y o= tros similares. La segunda semana de setiembre los participantes ingresaron de manera virtual los pesos de los residuos previamente clasificados con lo cu= al posteriormente se obtuvo la cantidad y composición de residuos generados en= tre el 9 y el 15 de setiembre. En este estudio de caracterización participaron = 17 personas de 3 distritos de la provincia de Panamá: Panamá (12), San Migueli= to (3) y Chepo (2).

 

 

Procedimiento de<= span style=3D'letter-spacing:-.1pt'> análisis de datos

 

Los resultados de la encuesta se analizaron porcentualmente. Una vez obtenido los pesos del grupo que participó, el procedimiento para el cálculo de la generación per cápita (GPC) y composici= ón de residuos se calculó siguiendo el método recomendado por el Cepis (Centro Panamericano de Ingeniería Sanitaria y Ciencias del Ambiente) (Cantanhede, Sandoval Alvarado, Monge, & Caycho Chumpitaz, 2005).

 

 =

= Resultados

 

Indicadores de generació= n de residuos sólidos

 =

 =

En la Tabla 1 se muestran los resultados de las preguntas hábitos de generación de residuos sólidos.

Indicadores de generac= ión de residuos sólidos

¿En qué tipo de recipiente saca los residuos sólidos de casa para entregar al camión recolector?

Bolsas plásticas

Bolsas de papel

Saco, costal u otro similar

Caja de cartón

Balde

75%

5%

8%

10%

3%

¿Cada cuántos días saca los residuos de casa?

Diario

2 días

3 días

4 días

Más de 5 días

21%

29%

19%

11%

21%

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 <= /span>

 <= /span>

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 <= /span>

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Tabla 1. Resultados de preguntas cerradas sobre hábitos de generación de residuos sólidos

 

Respecto al material usado para entregar los residuos al camión recolector el 75% emplea bolsas plásticas, 10% cajas de cartón, 8% sacos o costales y 5% bolsas de papel. El 21% saca sus residuos a diario, 29% cada dos días, 19% cada tres días, 11% cada cuatro días y 3% ca= da cinco o más días.

 

Percepción del servicio de recolección de residuos sólidos

 

En la Tabla 2 se muestran los resultados de la pregunta relativa a la percepción del servicio de recolección de residuos sólidos.

 

Percepción= del servicio de recolección de residuos sólidos<= o:p>

¿Cómo considera el servicio de recolección de residuos sólidos en tu municipio?=

Excelente

Bueno

Regular

Malo

Pésimo

6%

33%

43%

14%

3%

 

 

 

 

 

 <= /span>

 <= /span>

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Tabla 2. Resultados de pregunta sobre percepci= ón del servicio de recolección de residuos sólidos.

Sobre la calidad del servicio de recolección brindado por el municipio 43% lo considera regular, 33% bueno, 14% malo, 6% excelente y 3% pésimo. Las sugerencias para la municipalidad se refieren a aumentar la frecuencia de recojo (20%), definiendo días y cumpliendo con los horarios establecidos. Un respondiente del distrito Las Cumbres, provincia = de Panamá, indicó que en ocasiones recolectan los residuos cada dos semanas. Se solicita también renovar la flota de camiones recolectores y evitar que se rieguen lixiviados en la pista; así mismo que se recojan los residuos que puedan caerse del camión recolector durante la ruta. Finalmente se sugiere implementar el recojo de residuos segregados o aumentar los puntos donde po= der dejar residuos separados.

 

 

Indicadores de segregación de residuos sólidos

 

En la Figura 1 se presentan los resultados de las preguntas referentes a los hábitos de segregación de residuos sólidos.=

El 56% de los encuestados tiene capacitación o experiencia previa en segregación de residuos. El 57% sabe qué es un ecoladrillo. Antes de la pandemia el 50% de los respondientes entregaba los residuos inorgánicos generados en el domicilio a un reciclador (24% algunas veces, 14% en muchas ocasiones y 13% siempre). El 40% no entregaba sus resi= duos a un reciclador y el 10% manifestó que en su zona no hay recicladores. El 5= 7% no segrega los residuos que generan en el hogar; los participantes restantes separan sus residuos para reciclaje (14%), para reciclaje y orgánico (14%), para reciclaje y no aprovechable (8%) y, sólo orgánico (6%).

El 52% reúsa sus residuos orgánicos en la elaboración de compost (48%), como alimento para animales (17%), preparació= n de humus (5%) o productos de belleza (2%).

El 40% separa y almacena el aceite usado en la cocina. Este aceite almacenado es botado junto con el resto de residuos (48= %), llevado puntos de acopio de aceite usado (36%), y en dos casos empleado en = casa como combustible o en la elaboración de jabón.

Finalmente, en relación al uso de bolsas reutilizables para las compras, 76% usan bolsas de tela siempre, 22% en muc= has ocasiones y 2% algunas veces.

 

 

Figura 1. Resultados de preguntas sobre segregación de residuos sólidos

 

 

 

 

 

 

 

GPC domiciliaria

 

La GPC domiciliaria de la provincia de Panamá es 0.409 kg/hab./día, con una desviación estándar 0.23 y error del 27%. En la = Tabla 3 se presenta una comparación de la GPC domiciliaria de este estudio con ot= ros valores definidos para el distrito de Panamá entre el 2002 y el 2015 y la G= PC domiciliaria nacional del 2017.

 

Ámbito

Nacional

Distrito de Panamá

Provincia de Panamá

Año

2017

2002

2015

2020

GPC domiciliaria (kg/hab./día)

0.66a

0.590b

0.591c

0.409d

 

 

 

 

 

 

Tabla 3. Comparación de la GPC domiciliaria con valores del distrito de Panamá y nacional=

 

a (Ineco, 2017) / b (JICA, 2003) / c Proyección para el 2015 (JICA, 2003) / d Este estudio

 

Composición

 

En la Tabla 4 se presenta la composición de los residuos durante la cuarentena en la provincia de Panamá.=

 

 

Tipo de residuos

Porcentaje

1. RESIDUOS APROVECHABLES

 

1.1 Residuos orgáni= cos

43.99%<= o:p>

1.1.1 Residuos de preparación de alimentos y maleza

31.47%<= o:p>

1.1.2 Sobras de gui= sos de la comida, aderezos y huesos

12.52%<= o:p>

1.2 Residuos inorgánicos

34.67%<= o:p>

1.2.1 Polietileno

12.31%<= o:p>

1.2.2 Polietileno de alta densidad y polipropileno

4.28%<= o:p>

1.2.3 Residuos aprovechables diferenciados

10.14%<= o:p>

1.2.4 Ecoladrillo

3.83%<= o:p>

1.2.5 Aceite usado<= o:p>

4.11%<= o:p>

2. RESIDUOS NO APROVECHABLES

21.34%<= o:p>

2.1 Residuos sanita= rios

12.54%<= o:p>

2.2 Residuos peligr= osos

4.07%<= o:p>

2.3 Inertes

4.74%<= o:p>

Tabla 4. Composición de los residuos generados durante la cuarentena<= /span>

 

Sumando los sub totales para cada categoría se t= iene 43.99% de residuos orgánicos, 34.67% de residuos inorgánicos aprovechables y 21.34% de residuos no aprovechables. Las categorías con mayor proporción son los residuos de alimentos y malezas (31.47%); residuos sanitarios (12.54%); sobras de guisos y comidas (12.52%); polietileno (12.31%); y; residuos aprovechables diferenciados como papeles, empaques, vidrio o latas (10.14%)= .

 =

= Discusión

 

Percepción del servicio = de recolección de residuos sólidos

 

Como se refleja en las encuestas el servicio de recolección de los municipios en Panamá tiene muchos retos por delante, un diagnóstico hecho por la AAUD menciona que los municipios de las provincias= de Panamá Oeste, Colón y Herrera presentan deficiencias en la recolección de l= os residuos (AAUD, 2015). En el distrito de Chame, provincia de Panamá Oeste, un funcionario de la municipalidad manifestó que la concesionaria “al inicio del servicio … destinaba dos días de recolección a la semana, hoy en= día se ve casi un día al mes¨ (AAUD, 2015). En el municipio de Chagres, provincia de Colón= , no existe un sistema de recolección establecido de manera formal, por esta raz= ón los pobladores queman sus residuos o los disponen directamente en el verted= ero (AAUD, 2015). En la provincia de Panamá a excepción de los municipios de Panamá y San Miguelito, existen fuertes carencias en cuanto a personal y maquinaria para la recolección (AAUD, 2015) 

Indicadores de segregaci= ón de residuos sólidos

 

La proporción de aceite que se dispone junto con= el resto de residuos es preocupante pues en Panamá se estima que se generan alrededor de siete millones de galones de aceite al año, gran parte de los cuales termina en vertederos, ríos, quebradas y/ o en el suelo (DefensoríaDelPueblo, 2007).

 

GPC domiciliaria

 

En la Tabla 4 se observa que la GPC domiciliaria= de la provincia de Panamá es menor a los valores nacional y distritales. En mu= chas ciudades la cuarentena ha ocasionado un aumento en la generación de residuos domiciliarios producto del mayor consumo de productos a domicilio y compras= por internet (Pruett, 2020; Tenenbaum, 2020). Sin embargo, para un gran número de familias la cuarentena ha significado el cese de labores lo que ha llevado a una reducción de la capacidad adquisitiva del hogar (Ikiz, Maclaren, Alfred, & Sivanesan, 2021; Naughton, 2020)= . Esta reducción puede explicar la menor cantidad de residuos generad= os.

 

Composición

 

En términos de composición la única fuente de comparación para el estudio de caso está en el Plan Nacional de Gestión Integral de Residuos (Ineco, 2017). Contrastando ambos resultados se observa que la proporción de residuos orgánicos es mayor en e= ste estudio (34.67% nacional y 43.99% en este estudio). Esto puede deberse a qu= e al pasar mayor tiempo en casa haya aumentado la frecuencia y cantidad de preparación de alimentos lo que ha incrementado la cantidad de residuos orgánicos generados, así como las sobras de comida (Jribi, Ben Ismail, Doggui, & Debbabi, 2020).

La proporción de plásticos disminuyó ligeramente (17.20% nacional y 16.58% en este estudio). La proporción de residuos aprovechables diferenciados se redujo considerablemente (32.50% nacional y 10.14% en este estudio). Este último resultado tiene relación con la disminución de la GPC, explicada por una menor capacidad de adquisición familiar, en las familias al parecer se están comprando una menor cantidad = de productos empacados y procesados que usualmente tienen un mayor costo que l= os productos orgánicos (entendido como frutas, verduras y otros perecibles). <= o:p>

La cantidad de residuos peligrosos aumentó (1% nacional y 4.07% en este estudio). Para el estudio de caso los residuos peligrosos se componen en mayor proporción de mascarillas y guantes; en el = caso de las primeras se generaron un total de dos unidades por persona durante u= na semana, un promedio de siete mascarillas a la semana por familia. Es importante ten= er en cuenta este dato debido al riesgo de biocontaminación que presentan los residuos como mascarillas y guantes. Estudios confirman que el coronavirus puede sobrevivir en superficies de plástico entre 50 a 100 horas ADDIN CSL_CITATION {"citationItems":[{"id":"ITEM-1","itemDa= ta":{"DOI":"10.1016/j.jhin.2020.01.022","ISSN= ":"01956701","author":[{"dropping-particle&qu= ot;:"","family":"Kampf","given":&qu= ot;G.","non-dropping-particle":"","parse-name= s":false,"suffix":""},{"dropping-particle&quo= t;:"","family":"Todt","given":"= ;D.","non-dropping-particle":"","parse-names&= quot;:false,"suffix":""},{"dropping-particle"= :"","family":"Pfaender","given":&qu= ot;S.","non-dropping-particle":"","parse-name= s":false,"suffix":""},{"dropping-particle&quo= t;:"","family":"Steinmann","given":= "E.","non-dropping-particle":"","parse-n= ames":false,"suffix":""}],"container-title&qu= ot;:"Journal of Hospital Infection","id":"ITEM-1","issue":"3= ","issued":{"date-parts":[["2020","= 3"]]},"page":"246-251","title":"Per= sistence of coronaviruses on inanimate surfaces and their inactivation with biocidal agents","type":"article-journal","volume"= ;:"104"},"uris":["http://www.mendeley.com/document= s/?uuid=3Dacce1ff6-89e4-41fb-9ec0-238943c621ac"]},{"id":&quo= t;ITEM-2","itemData":{"DOI":"10.1056/NEJMc200= 4973","ISSN":"0028-4793","author":[{&quo= t;dropping-particle":"","family":"Doremalen&q= uot;,"given":"Neeltje","non-dropping-particle"= ;:"van","parse-names":false,"suffix":"&q= uot;},{"dropping-particle":"","family":"= Bushmaker","given":"Trenton","non-dropping-pa= rticle":"","parse-names":false,"suffix":= ""},{"dropping-particle":"","family"= ;:"Morris","given":"Dylan H.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""},{"dropping-particle":= "","family":"Holbrook","given":&quo= t;Myndi G.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""},{"dropping-particle":= "","family":"Gamble","given":"= Amandine","non-dropping-particle":"","parse-n= ames":false,"suffix":""},{"dropping-particle&= quot;:"","family":"Williamson","given&qu= ot;:"Brandi N.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""},{"dropping-particle":= "","family":"Tamin","given":"A= zaibi","non-dropping-particle":"","parse-name= s":false,"suffix":""},{"dropping-particle&quo= t;:"","family":"Harcourt","given":&= quot;Jennifer L.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""},{"dropping-particle":= "","family":"Thornburg","given":&qu= ot;Natalie J.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""},{"dropping-particle":= "","family":"Gerber","given":"= Susan I.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""},{"dropping-particle":= "","family":"Lloyd-Smith","given":&= quot;James O.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""},{"dropping-particle":= "","family":"Wit","given":"Emm= ie","non-dropping-particle":"de","parse-names= ":false,"suffix":""},{"dropping-particle"= ;:"","family":"Munster","given":&qu= ot;Vincent J.","non-dropping-particle":"","parse-names&q= uot;:false,"suffix":""}],"container-title":&q= uot;New England Journal of Medicine","id":"ITEM-2","issue":"16= ","issued":{"date-parts":[["2020","= 4","16"]]},"page":"1564-1567","titl= e":"Aerosol and Surface Stability of SARS-CoV-2 as Compared with SARS-CoV-1","type":"article-journal","volume&= quot;:"382"},"uris":["http://www.mendeley.com/docu= ments/?uuid=3D02552489-4f66-460d-98ea-ebdba73c478a"]}],"mendeley&= quot;:{"formattedCitation":"(Kampf, Todt, Pfaender, & Steinmann, 2020; van Doremalen et al., 2020)","plainTextFormattedCitation":"(Kampf, Todt, Pfaender, & Steinmann, 2020; van Doremalen et al., 2020)","previouslyFormattedCitation":"(Kampf, Todt, Pfaender, & Steinmann, 2020; van Doremalen et al., 2020)"},"properties":{"noteIndex":0},"schema&= quot;:"https://github.com/citation-style-language/schema/raw/master/cs= l-citation.json"}(Kampf, Todt, Pfaender, & Steinmann, 2020; van Doremalen et al., 2= 020). La Organización Panamericana de la Salud (OPS, 2020) ha emitido recomendaciones para la disposición de residuos que reduzcan el riesgo de contaminación por parte de los trabajadores del servicio de recolección de residuos. Aunque tangencialmente y de manera muy sucinta los Ministerios de Salud (Minsa, 2020c) y del Trabajo = (MinisteriodeTrabajoyDesarrolloLaboral, 2020) de Panamá también han dado recomendaciones para la gestión de residu= os durante la pandemia.

 

Conclusiones<= /span>

 

La encuesta realizada a participantes de seis provincias de Panamá devela las deficiencias que presenta el servicio de recolección de residuos en diferentes zonas del país. Solamente la mitad de= los encuestados segrega sus residuos y los entrega a un reciclador o los deposi= ta en algún punto de acopio.

La GPC domiciliaria de la provincia de Panamá es 0.409 kg/hab./día, este valor representa una disminución respecto a valores hallados previamente a nivel nacional y para el distrito de Panamá. Dicha reducción puede deberse a una menor capacidad de adquisición familiar produ= cto del desempleo ocasionado por la cuarentena.

En cuanto a la composición de residuos el mayor porcentaje (43.99%) lo representan los residuos orgánicos, seguido de los residuos inorgánicos aprovechables (34.67%) y por último los residuos no aprovechables (21.34%). Comparando estos valores con los presentados el año 2017 en el Plan Nacional de Gestión Integral de residuos la proporción de residuos orgánicos y peligrosos aumentó, la de plásticos se mantuvo similar= y la de residuos aprovechables disminuyó. Los residuos orgánicos pueden haber aumentado por una mayor frecuencia y cantidad de alimentos preparados en ca= sa. El aumento de los residuos peligrosos es un tema al que debe de prestarse e= special atención debido al riesgo que puede representar el manejo de residuos biocontaminados por parte del personal de servicio de recolección de residu= os.

Cabe resaltar que el grupo seleccionado como mue= stra para la recopilación de datos son estudiantes universitarios familiarizados= con el tema de gestión de residuos sólidos y temas ambientales, lo que ayuda a obtener mejores datos para el procesamiento.

=  

= Referencias

 

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Nor= vin Requena Sánchez, et al. = DOI: https://doi.org/10.37387= /ipc.v9i2.232 <= /span>

Norvin Requena Sánchez, et al. DOI: https://doi.org/10.37387= /ipc.v9i2.232

 

Invest. pens. crit. ,2021, 9 (2), 16-24          =      

                                               =                                                                                                 24

 

=  

= Invest. pens. crit. ,2021, 9 (2), 16-24

                                                =                                                                            =                                     17

 

Invest. Pens. Crit. (ISSN 1812-3864; eISSN 2644-4119)

Vol. 9, No. 2, Mayo – Agosto 2021. pp. 16 -24

DOI: = https://doi.= org/10.37387/ipc.v9i2.232

Artículo Científico

Invest. pens. crit. ,2021, 9 (2), 16-24                                                                                               =                                                              = 16

 

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