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Identificación y análisis de microplásticos en la zon= a costera de Playas (General Villamil), provincia del G= uayas, Ecuador<= o:p>

<= o:p> 

= Identification and = analysis of microplastics in the

coastal= zone of Playas (General Villamil),

 

Acta Oceanográfica del Pací= fico

DOI: https://doi org/ 10.54140/raop.v7i1.86

Recibido: 09 de mar= zo, 2024

Aceptado: 28 de enero, 2025=

Vol 7. No. 1 2025

ISSN: 1390-129X<= /span>

ISSN: 2806-5522 =

Pg. 61-81=

 

 
= Guayas province, Ec= uador= <= /span>

 

David Segarra Vera

Lcdo. en Gestión de Transporte

Universidad Del Pacífico

Facultad del Mar y Medio Ambiente

Guayaquil- Ecuador

david.segarra@upacifico.edu.ec

ORCID: https://orcid.org/0009-0005-<= /span>9949-5553

Teresa Vera San Martín

Oceanógrafa=

Escuela Superior Politécnica del Litoral, ESPOL

Centro Internacional del Pacífico para la Reducción del Riesgo de Desastres=

Campus Gust= avo Galindo

Km 30.5 Vía Perimetral, Guayaquil, 090902, Ecuador

tvera@espol= .edu.ec

ORCID: https://orcid.org/0000-0002-9891-6548

Dolores Astudillo Brocel

Ingeniera Industrial<= span style=3D'mso-bookmark:_Hlk191042092'>

Master en Ciencias en Ingeniería Ambiental y Energía

Universidad= Del Pacífico

Facultad del Mar y Medio Ambiente

dolores.ast= udillo@upacifico.edu.ec

ORCID: https://orcid.org/0000-0002-2120-6687

Mario Palacios Moreno

Biólogo

Universidad Del Pacífico

Facultad del Mar y Medio Ambiente

Guayaquil-Ecuador

mario.palacios@upacifico.edu.ec

ORCID: https://orcid.org/0000-0002-0= 440-3822

 

Resumen

<= span style=3D'mso-bookmark:_Hlk190773182'>= Los microplásticos son partículas de plástico que miden de 1 a 5 mm, se pueden encontrar en la arena de las playas y en otros lugares de la naturaleza y plantean graves problemas medioambientales y de salud. Como marco metodológ= ico se aplicó el EPA’s Micropl= astic Beach Protocol para recolección y análisis de muestras de arena con el fin de determinar la presencia de microplásticos e= n el sector malecón de Playas Villamil, en la provincia del Guayas, Ecuador. Se presentan los resultados de tres muestreos realizados en noviembre de 2021, mayo y agosto de 2022. Se identificaron cinco tipos de microplásticos que s= on: Fragmentos, pellets, microfibras, películas plásticas y espumas. De los tre= s muestreos, en noviembre de 2021 se detectó la mayor cantidad de microplásticos y se registraron menores cantidades en mayo y agosto de 2022, respectivamente. La investigación sugiere una influencia estacional en la distribución y acumulación de microplásticos. Los hallazgos plantean la necesidad de ampli= ar el alcance geográfico y la frecuencia de los estudios para comprender mejor= la magnitud del problema y desarrollar estrategias efectivas de prevención y mitigación. Se subraya la importancia de adoptar medidas preventivas y correctivas para abordar esta problemática global.=

 

Palabras clave= :=   Microplásti= cos, contaminación, fragmento, playa, salud.

 

= Abstract

Microplastics are plastic particles that measure 1 to 5 mm, can be found in the sand on beaches and in other places in nature and pose serious environmental and health problems. = As a methodological framework, the EPA's Microplastic Beach Protocol was applied= to collect and analyze sand samples to determine the presence of microplastics= in the Malecon sector of Playas Villamil, in the province of Guayas, Ecuador. = The results of three samplings conducted in november 2021 and may and august 2022 are presented. Five typ= es of microplastics were identified: fragments, pellets, microfibers, plastic fil= ms and foams. Of the three samplings, the highest amount of microplastics was detected in november 2021 and lower amounts were recorded in may and august 2022, respectively. The research suggests a seas= onal influence on the distribution and accumulation of microplastics. The findin= gs indicate the need to expand the geographic scope and frequency of surveys to better understand the magnitude of the problem and develop effective preven= tion and mitigation strategies. It underscores the importance of taking preventi= ve and corrective measures to address this global problem.

 

Key words: Microplastics, pollution, fragment, beach, health.

 =


= Introducción=

La presencia de microplásticos en las costas tiene diversas afectaciones ambientales, ecológicas y potencialmente nocivas para la salud humana. La definición de microplástico aún carece de un consenso universal. No obstant= e, para fines de monitoreo, el Grupo Conjunto de Expertos sobre los Aspectos Científicos de la Contaminación Marina (GESAMP, 2019) 

Los microplásticos, que provienen de la descomposición de plásticos más grandes= y de productos de consumo como cosméticos y ropa sintética, pueden ser ingeri= dos por la fauna marina, causando dańo físico y tóxico a organismos como peces, aves, moluscos y crustáceos, entre otros. Esta contaminación afecta la cade= na alimentaria, ya que los microplásticos y las sustancias químicas pueden bioacumularse y biomagnificarse, llegando eventualmente a los humanos que consumen productos del mar (ONU, 2023).

(UNEP, 2009) 

= Según Gaibor et al., (2020), en un estudio realizado en las playas de Ecuador, en la mayoría de estas  

= Los microplásticos, al ser partículas diminutas que se encuentran en fragmentos de menos de 5 mm, pueden ser ingeridos por organis= mos acuáticos y terrestres y persistir a lo largo de la cadena alimenticia. Las especies marinas confunden su alimentación con trozos de microplásticos ya = que estos se asemejan a presas o al ser menos visibles en el contexto de aguas abiert= as donde se alimentan (Schuyler et al., 2014). Las tortugas marinas ingieren principalmente plásticos blancos y transparentes, además de polímeros con una densidad inferior a la del agua de mar, como el polietileno, el polipropileno, y sus copolímeros (Moon et al., 2023)= .

 

= Los microplásticos representan un riesgo para la salud humana debido a la exposición a diversas sustancias químicas tóxicas presen= tes en ellos, las cuales pueden ingresar al organismo por ingestión, inhalación= , o contacto dérmico (Azoulay et al., 2019). Un estudio de biomonitorización proporcionó la primera medición de la concentración de masa del componente polimérico del plástico en sangre huma= na, evidenciando la absorción sistémica de partículas plásticas biodisponibles = en algunos alimentos. (Leslie, 2022)

=  

= El propósito de este artículo es evaluar las características y distribución de microplásticos en la arena de un tramo del frente de la playa de Playas (General Villamil), en el periodo noviembre 20= 21 a agosto de 2022.

=  

Materiale= s y Métodos

= Área de estudio= =

= El monitoreo fue realizado en General Villamil, cabec= era cantonal del cantón Playas en la provincia del Guayas; la zona de estudio se localiza al sur de la región litoral del Ecuador, con coordenadas 2°38̸= 2; S y 80°23′ O.

General Villamil (generalmente conocido como Playas) es una ciudad costera en el Ecuador, su borde marino se extiende en sentido NO – SE por 14 Km de playas con arenas finas, que van de desde la ciudad hasta el poblado de Data Poso= rja, en el extremo sur de la provincia de Guayas . La playa en la que se realizó este trabajo es de tipo urbana (según la clasificación de

=  

La zona de playa para = la toma de muestras se ubicó a la altura de la explanada del malecón (Figura 1= ). Las coordenadas del inicio del transecto son 2° 38´13.63” S y 80° 23´35.24”= O y su extensión es de 100 metros paralelos a la línea de agua como se recomien= da en estudios previos (Uhrin et al., 2022)= . Se muestreó por 3 ocasiones, en los meses de noviembre de 2021 y mayo y agosto= de 2022, para determinar la presencia y tipo de microplásticos en esa zona costera.


 



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Figura 1. Ubicación del área de estudio. La línea roja segmentada representa el transecto.=

 

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= Recolección de datos

La metodología empleada es la propuesta por= “EPA’s= Microplastic Beach Protocol. A Community Science Protocol for Sampling Microplastic Pollution” (EPA’s Microplastic Beach P= rotocol, 2021).=

 <= /o:p>

Se organizaron las fechas y horas de muestr= eo de modo que se realizaran una hora después de la marea alta para no tener interferencia de las olas y poder determinar fácilmente la línea de agua de= la pleamar.

 

Se seleccionaron cinco sitios a lo largo del transecto de 100 metros, siguiendo una línea imaginaria “Last hide tide/ Wr= ack line” (EPA’s Microplast= ic Beach Protocol, 2021) coincidente con la línea de la última marea alta. El espaciamiento entre ca= da uno de los 5 sitios de muestreo es aleatorio para lo cual se siguió un procedimiento específico basado en el método de referencia y se determinó s= olo en la primera campańa, quedando así definidos los sitios de muestra para to= do el estudio. Se utilizó un cuadrante de madera de 50 x 50 cm de lado, coloca= do en cada uno de los cincos sitios a lo largo del transecto de 100 metros, en donde se recolectaron muestras de arena.

 

A fin de prevenir= la contaminación de cada muestra por microfibras plásticas liberadas por la ro= pa del grupo de muestreo, al momento de recoger la arena los recolectores consideraron la dirección del viento y se colocaron a sotavento del cuadran= te de muestreo.

 =

En cada sitio de muestreo, una vez colocado el cuadrante de madera sobre la superficie de la arena, se cavó dentro de él hasta una profundidad de 7 cm, lo que se verifi= có realizando la medición con una regla metálica. Una vez verificada la profundidad, se recogió la muestra de arena de toda la superficie del cuadrante, para esto, se empleó una pala de metal y se depositó la muestra = de arena en un recipiente limpio de aluminio.

Según lo describe= el método empleado como referencia, se extrajeron cuidadosamente del cuadrante= de muestreo elementos grandes como conchas, madera, algas o piedras antes de t= omar la muestra (EPA’s Microplast= ic Beach Protocol, 2021). 

 =

Luego de completa= r la cantidad de muestra requerida (2 kg), se cubrió completamente cada recipien= te con papel aluminio para evitar su contaminación. Se rotuló cada recipiente incluyendo en la etiqueta el número de cuadrante y la fecha de la toma de m= uestra. Para el etiquetado se utilizó la codificación con la letra “P” más # de cuadrante, así se obtuvieron muestras identificadas como P1 a P5.

=  

= Preparación de muestra

Todas las muestras recolectadas se trasladaron al laboratorio y se mantuvieron en reposo por d= os días con el propósito de que se evapore la humedad, luego se realizó cuidadosamente la separación, pesado, identificación y análisis de las muestras, y se tuvo la precaución de no utilizar plásticos o productos derivados del plástico para no contaminar las muestras.

 =

= Separación de muestras y materiales en el laboratorio= .

En el laboratorio se realizó el pesado de un 1 kilo de arena por cada muestra, luego se las pasó a través de un tamiz de 5 mm y de otro de 1 mm de diámetro de ojo de malla (Anexo B).

 

Luego de tamizar las muestras se retuvo lo que se encontró en los tamices de 1 y 5 mm, el resto (la arena) se descarta, queda= ndo así dos muestras: lo retenido del tamiz de 5 mm y lo retenido en el tamiz de 1mm.

 

Después, los contenidos de cada tamizado de las muest= ras se colocaron dentro de una solución salina que se preparó disolviendo completamente dos cucharadas de cloruro de sodio (NaCl) en un litro de agua dentro de un recipiente de vidrio, el recipiente usado fue de tipo bandeja = que permite una “amplia superficie”. Allí se colocó el material retenido en los tamices, para esperar a que los plásticos de tamańo micro floten en el recipiente, de modo que sean visibles y cuantificables. Al mismo tiempo se documentó los hallazgos con fotografías y en las hojas de registro.

 

 = Identificación de microplásticos en muestras= .

Para la identificación de los microplásticos se reali= zó previamente la familiarización con cada uno de los tipos de microplásticos definidos en la metodología (EPA, 2021), los cuales son:<= /p>

 

ˇ&nb= sp;        Fragmento: Se represen= ta en muchos tipos de plásticos y pueden volverse quebradizos con el tiempo. <= o:p>

ˇ&nb= sp;        Pellets: Son usados en= la fabricación de plástico, tienen un aspecto redondo y pueden tener diferentes colores, pero los más comunes son negros y blancos.

ˇ&nb= sp;        Microfibras: Son fibras plásticas procedente de textiles y cuerdas y se presentan en varios colores= .

ˇ&nb= sp;        Película plástica: Son trozos de bolsas y envoltorios plásticos, son flexibles y pueden volverse quebradizo con el tiempo.

ˇ&nb= sp;        Espuma: Son trozos de poliestireno y generalmente tiene una textura suave.

 

Se empleó en el laboratorio material de apoyo impreso (guías) en las que constan las distintas clases de microplásticos que se han identificado en la literatura científica sobre el tema (Anexo A). Se identificaron visualmente los microplásticos, observando los bordes y la superficie del recipiente con la solución salina en donde se colocaron las muestras, ya que los microplásticos tienden a flotar y acumularse en los bo= rdes por el exceso de sal y debido a su menor densidad.

 

Para retirar los microplásticos de la solución salina= se empleó una pinza metálica. Al introducir la pinza en el recipiente para rec= oger los microplásticos, estos se desplazaron hacia esta.

Para optimizar la tarea de identificación y extracció= n de los microplásticos flotantes se colocó papel negro en el fondo del recipien= te, se apagó la luz del laboratorio y se usó una linterna cerca de la superficie del agua para poder identificar microplásticos de tipo: Fragmento, espuma, microfibras o película de plástico, que pueden ser transparentes y de difíc= il detección a simple vista.

 

Posteriormente, para realizar la clasificación, se re= tiró el microplástico del recipiente usando las pinzas, se lavó con agua utiliza= ndo un cernidor pequeńo y se colocó sobre un papel secante para escurrir el exc= eso de agua. Se dejó reposar.

Con la asistencia de un lente de aumento, se determin= aron las dimensiones máximas de los microplásticos, en longitud y en anchura, y = se procedió a su clasificación. Utilizando una hoja de datos, se registró la información específica de los microplásticos en cada cuadrante. La informac= ión recopilada durante la identificación de los microplásticos incluyó: número = del cuadrante, peso, tipo, tamańo (talla: largo y anchos máximos), color y diám= etro del tamiz utilizado.

Obtenidos los resultados de cada uno se fotografiaron= y separaron por grupos, en consideración al mes y el ańo del muestreo (Anexo = C). Las fotografías también se separaron por grupos en un documento para tener = los registros organizados.

<= span class=3DFuentedeprrafopredeter1>=  

= Resultados=

Al analizar las muestras se identificaron un total de= 28 partículas de microplásticos en Playas Villamil, en las campańas de noviemb= re de 2021, mayo y agosto de 2022. Estos corresponden a la temporada seca (noviembre de 2021), fin de la temporada lluviosa (mayo, 2022) y temporada = seca de ańo siguiente (agosto de 2022).

 

 Muestreo realizado en noviembre de 202= 1.

El primer muestreo se realizó el 6 de noviembre de 20= 21, en la temporada seca, la cual se caracteriza por la ausencia de precipitaciones. En el tamiz de 1 mm se identificaron 6 fragmentos de microplásticos, éstos se encontraron en los cuadrantes P2, P3, P4 y P5, de colores blanco, negro, verde y amarillo. Así mismo, se encontraron 3 microfibras en los cuadrantes P1, P2, y P5 de color azul, café y blanco, co= mo se muestra en la (Tabla 1).

 

 


 

 

 

 

 

 

 

 

 

 

 

 

Tabla 1. Resultados de muestras de arena en el mes de noviembre empleando tamiz de 1 mm

Datos de microplásticos en muestra de noviembre de 2021 

Cuadrante

Peso (g)

Tipo

Talla (mm) <= o:p>

Color= =

P1

1090

Microfibra

1*9

Azul

P2

1422

Fragmento

7*9

Blanco<= /o:p>

Fragmento

7*8

Blanco<= /o:p>

Pellets=

1*2

Negro

Pellets=

1*2

Negro

Pellets=

1*1

Negro

Microfibra

3*22

Blanco<= /o:p>

P3

1274

Pellets=

5*5

Blanco<= /o:p>

Fragmento

2*2

Amarillo

P4

1422 

Fragmento

1*2

Verde

Fragmento

1*2

Verde

Pellets=

1*3

Negro

Pellets=

1*1

Negro

P5

561 

Fragmento

3*6

Café

Microfibra

1*14

Café


Se puede observar las diferencias de tamańos de cada partícula de microplásticos, la más grande fue de tipo microfibra con un ta= mańo de 3 por 22 mm y otros fragmentos de 7 por 9 mm y 7 por 8 mm, también se registró un pellet con un tamańo de 5 por 5 mm, seguido por un fragmento de= 3 por 6 mm y los más pequeńos fueron pellets, fragmentos y microfibras con un tamańo de 1 por 14 mm.

 

Muestreo realizado en mayo de 2022.

Para las muestras tomadas en mayo, se obtuvieron diferentes tipos de microplásticos entre ellos 2 películas de plástico de c= olor gris oscuro y blanco, los mismos que fueron encontrados en los cuadrantes e= n P1 y P4. También se encontró un microplástico de tipo espuma en el cuadrante P4 (Tabla 2).

 

Se identificó una microfibra y también una película plástica en el cuadrante P3. En el cuadrante de P5 se registraron tres microplásticos de tipo fragmentos 

Se pueden observar las diferencias de tamańo de los microplásticos el más grande fue el fragmento con un tamańo de 8 por 4 mm, seguido por un fragmento con un tamańo de 5 por 2 mm y una espuma con un ta= mańo de 5 por 3 mm, una microfibra de un tamańo de 3 por 5 por 1 mm y pellets de= un tamańo de 1 por 1 mm y un fragmento con el mismo tamańo.<= /p>

 


 

Tabla 1. Resultados de mue= stra de arena en el mes de mayo en el tamiz de 1mm. =

Cuadrante

Peso (g)

Tipo

Talla (mm)

Color

P1

98.9 

Película plástica

2.5*2

Gris Oscuro

P2

92.2

--

--

--

P3

92.5

Microfibra

3.5*1

Azul

P4

98.9 

Espuma

5*3

Blanco

Película plástica

2*1.5

Blanco

Pellets

3*3

Negro

Pellets

1*1

Blanco

P5

93.4

Fragmento

8*4

Blanco

Fragmento

5*2

Blanco

Fragmento

1*1

Blanco

 


Muestreo realizado en agosto de 2022.

En el cuadrante P1 se registró un microplástico de ti= po fragmento. En el cuadrante P2 se registró un filamento y en el cuadrante P5= se registró una microfibra y una película plástica. 

 

Se puede observar las diferencias de tamańo de cada partícula de microplástico, el más grande de los microplásticos fue un fragmento con un tamańo de 4 por 1 mm, seguido por un fragmento con un tama= ńo de 1 por 3 mm, microfibras de 1 por 1 mm y una película plástica de 1 por 1= mm.


Tabla 2. Resultados de muestra de arena en el mes agosto en el tamiz de 1mm.

Cuadrante

Peso (g)

Tipo

Talla (mm)

Color

P1

1579)

Fragmento

4*1

Blanco

P2

1667

Fragmento

1*3

Negro

P3

1233

--

--

--

P4

1636

--

--

--

P5

1360

Microfibras

1*1

Blanco

Película plástica

1*1

Azul

 


En el cuadrante de P2 del mes mayo de 2022= no se registró ningún microplástico al realizar el tamizado con los tamices de= 1 y 5 mm.  =

En los cuadrantes de P3 y P4 del mes de ag= osto de 2022 tampoco se registró ningún microplástico. =

En l= os tamices de 1 y 5mm, en los muestreos de mayo y agosto, se encontraron fragmentos de madera y carbón, que se descartaron por no ser de interés par= a el análisis.

 

Se analizaron diferentes tipos de microplásticos y se encontró que las microfi= bras tienen las mayores dimensiones, con un tamańo de 3 por 22 mm. Los fragmentos, pellets y películas plásticas tienen dimensiones menores, c= on tamańos de 8 por 4 mm, 5 por 5 mm y 2.5 por 2 mm, respectivamente.

 

Los resultados de este estudio evidencian la presencia continua y diversa de microplásticos en la zona costera de Playas (General Villamil), destacando = la contaminación por microplásticos en tres campańas de muestreo diferentes: noviembre de 2021, mayo de 2022 y agosto de 2022 (Figura 2). La identificac= ión de 28 partículas de microplásticos en total subraya la importancia de monitorear el problema y la influencia de factores estacionales. En la temporada seca de noviembre de 2021, se encontraron principalmente fragment= os y microfibras de diversos colores y tamańos.





 

 <= /span>

Figura 2. Distribución obtenida por mes en la identificación de microplásticos.


En l= os tres meses se obtuvo en todas las muestras diferentes tipos de microplástic= os documentados: microfibras, fragmentos, pellets, película plástica y espuma, todos retenid= os en el tamiz de 1 mm; en el tamiz de 5 mm no se retuvieron microplásticos, p= ero en ambos tamices (de 1 y 5mm) se encontraron diferentes tipos de elementos como: madera, carbón y semillas.

 

Noviembre: Refleja un total de 15 unidades de microplásticos en los cuadrantes P1, P2 y P5; 3 unidades de microfibras detectadas en los cuadrantes P1, P2 y P5; 6 unidades de fragmen= tos en los cuadrantes de P2, P3, P4 y P5, finalmente 6 unidades de pellets en l= os cuadrantes de P2, P3 y P4. 

Mayo: Refleja un total de 9 unidade= s de microplásticos obtenidos en los cuadrantes P1, P3, P4 y P5. Se encontraron 2 películas plásticas en los cuadrantes P1 y P4; 1 espuma en el cuadrante P4;= 1 microfibra en el cuadrante P3; 2 pellets en el cuadrante P4 y, 3 fragmentos= en el cuadrante P5. Agosto refleja un total de 4 unidades de microplást= icos obtenidos en los cuadrantes P1, P2 y P5: 1 fragmento en el cuadrante P1, ot= ro en el cuadrante P2 y 1 microfibra y 1 película plástica en el cuadrante P5.=

= Colores en los microplásticos

El color predominante en las muestras de microplásticos fue el blanco, con 40%, seguido por el negro, 24%. Estos dos fueron los colores más frecuentes de los microplásticos en las muestras, seguidos por el color verde con 13 %, azul 10%, café 7%, amarillo y gris co= n un 3%, cada uno. Esta distribución se representa en la (Figura 3).<= /span>


 

=

Figura 3. Color de muestra de microplásticos en los 3 meses.=

 


Más = de la mitad de los microplásticos identificados (64%) fueron de color blanco o negro, el restante porcentaje (36%) se distribuyó entre otros cinco colores= en las proporciones seńaladas.

 

Densidad de microplásticos en las muestras.

La presencia de microplásticos por metro cuadrado puede variar dependiendo del lugar y de la fuente de contaminación, así como del tamańo del grano de are= na. Para estimar la cantidad de microplástico por metro cuadrado en este trabaj= o, se extrapolaron los valores encontrados en cada cuadrante, en el área de la playa de General Villamil.

 

La T= abla 4 presenta los valores de cada muestra con el promedio total por metro cuadrado. Se observó que, en noviembre de 2021, se obtuvo un promedio de 12= microplásticos por cada metro cuadrado, en el mes de mayo de 2022 se obtuvo un promedio de= 7.2 y en el mes de agosto 2022 se obtuvo en promedio de 3.2 microplásticos por metro cuadrado. Los valores fueron disminuyendo según la secuencia de muest= reo desde noviembre a agosto. Como promedio de los valores se obtiene 7.47 unid= ades de microplásticos por metro cuadrado.


 

Tabla 3. Microplásticos por metro cuadrado.<= /span>

 

Microplásticos por metro cuadrado

P1=

P2=

P3=

P4=

P5=

Promedio

nov-21=

4

24

8

16

8

12

may-22=

4

0

4

16

12

7.2

ago-22=

4

4

0

0

8

3.2

Promedio total anual

7.47

 


= Discusión

La variabilidad en el tipo de microplásticos, como películas plásticas, espuma= s y filamentos, observada en mayo y agosto de 2022, sugiere la necesidad de may= ores estudios para terminar el origen y las vías de llegada de los microplástico= s.

 

Las implicaciones de estos hallazgos son significativas. La identificación de diferentes tipos de microplásticos a lo largo de las estaciones sugiere que= las fuentes de contaminación son variadas y probablemente incluyen tanto actividades locales como la llegada de residuos a través de corrientes oceánicas y mareas. Sin embargo, este estudio también tiene sus limitacione= s; por lo que se resalta que el número de muestras, la extensión de la zona de muestreo y la metodología de recolección podrían influir en los resultados,= y la no realización de análisis químicos detallados de los polímeros específi= cos limita la capacidad de identificar con precisión las fuentes exactas de los microplásticos.

 

Estos hallazgos encajan en el contexto de investigaciones globales que muestran un aumento constante en la contaminación por microplásticos en diversas region= es costeras. Comparado con estudios similares en otras partes del mundo, los resultados de Playas Villamil confirman una tendencia preocupante que requi= ere una acción urgente y coordinada. Para futuras investigaciones, sería beneficioso ampliar el alcance temporal y espacial del muestreo, incluir análisis químicos detallados para identificar tipos específicos de polímero= s, y estudiar los impactos ecológicos directos en la fauna marina local. Además,= es crucial desarrollar e implementar estrategias efectivas para la gestión y reducción de plásticos, involucrando tanto a las comunidades locales como a= las autoridades gubernamentales.

 

La manera cómo los diversos colores de los plásticos y los microplásticos, afe= cta al ecosistema y a las especies, se ha reportado previamente, en estudios como el de la Universidad de Exeter, Reino Unido, en el que se estableció que especies como las tortugas marinas confunden sus alimentos= con los plásticos, hallándose en sus tractos gastrointestinales plásticos de co= lor verde y negro, incluso más de 180 piezas. Las tortugas pueden tragar los residuos del plástico de colores naturales, ya que los confunden con algas marinas y medusas (Duncan, 2019).

 

Los peces pueden confundir los microplásti= cos con alimentos debido a su alta concentración o a su color, que puede ser similar al de sus presas. Por ejemplo, los microplásticos azules pueden ser confundidos con el zooplancton. Esta confusión puede llevar a la ingestión accidental de microplásticos. En el tracto digestivo de los peces, se han encontrado principalmente fibras, seguidas de fragmentos. Los colores predominantes son el azul y el rojo (Mazariegos et al., 2021).

 

Estas referencias evidencian que colores como el verde, negro y azul en materiales como microplásticos y plásticos han sido identificados en la ingesta de especies acuáticas, representando estos colores el 47% en los resultados del presente estudio. = La alta dinámica de la zona costera plantea una amenaza real por la transferencia de los microplásticos entre costa y océano. Se evidencia también con este resultado la necesidad de estudios de los efectos de los microplásticos, sus colores y sus tipos, en las especies y hábitat de la zona de playa.  

 

En noviembre de 2= 021, la densidad de 12 microplásticos por metro cuadrado coincide con la tempora= da alta de turismo en Playas (General Villamil), cuando se incrementa el númer= o de visitantes; el muestreo se llevó a cabo el 13 de noviembre, una semana desp= ués de uno de los feriados más largos correspondiente al Día de los Difuntos y = la independencia de Cuenca. Además, es relevante mencionar que el calendario de aguajes 2021 indica que los primeros días del mes de noviembre se presentó = un máximo aguaje en ese ańo.

=  

En contraste, la disminución a 7.2 microplásticos por metro cuadrado en mayo de 2022 coincide con el final de la temporada turística y el comienzo de la temporada seca, = que suele atraer menos turistas, El muestreo se realizó el 14 de mayo, una sema= na después del aguaje.

 =

En agosto de 2022= , se registró un promedio significativamente menor de 3.2 microplásticos por met= ro cuadrado, la disminución coincide con el periodo posterior a la temporada a= lta, donde la menor actividad turística contribuye a la reducción de microplásti= cos en la playa. El muestreo se realizó el 13 de agosto, durante los días de má= ximo aguaje. Es relevante seńalar que el calendario de aguajes del 2022 indica q= ue hubo tres días de máximo aguaje en esas fechas.

 =

Estos patrones sugieren una coincidencia entre la actividad turística y la presencia de microplásticos, destacando la importancia de implementar técnicas y métodos sistemáticos de monitoreo, muestreo y análisis. Se enfatiza la necesidad de estrategias de manejo de residuos durante los picos turísticos para mitigar= la contaminación en esta zona costera.

 =

Las concentracion= es de microplásticos en la zona muestreada fueron significativamente menores q= ue las presentadas como referencia por (Jones, 2022) para otras zon= as costeras del Pacífico como México, Panamá, Colombia y Perú, en las que se triplican y en algunos casos son hasta un orden de magnitud mayores. Los hallazgos son similares a los encontrados en las costas de Chile, enfatizan= do que son valores referenciales, ya que no es posible una comparación precisa= por la diferencia en método y diseńos de muestreo.

 =

Al comparar los resultados obtenidos para las concentraciones de microplásticos por metro cuadrado en Playas Villamil con estudios realizados en las Islas Galápagos, se observan tanto similitudes como diferencias significativas en la presencia y tipos de microplásticos. La concentración media de partículas en Punta Pitt alcanzó = 381 ą 68 partículas por metro cuadrado, en Tortuga Bay fue 74 ą 43; en comparac= ión, en la playa de General Villamil tuvo un promedio de 7.47 partículas por met= ro cuadrado, una tasa mucho menor comparada con las playas de las Islas Galápa= gos. Con respecto a los tipos de microplásticos y sus colores, en Playas Villami= l, se identificaron microfibras, fragmentos, pellets, película plástica y espu= ma, con predominancia de colores blanco y negro. En el caso de l= as Islas Galápagos, los análisis realizados indican una predominancia de pelle= ts plásticos en Tortuga Bay y fragmentos en Punta Pitt, los fragmentos encontr= ados eran incoloros y el color de los pellets encontrados eran incoloros, blanco= s o amarillos.

<= span lang=3DES style=3D'font-size:12.0pt;mso-bidi-font-size:11.0pt;font-family:"= Arial",sans-serif; mso-ansi-language:ES'> 

Estudios como el de Jones et al., (2022) apuntan a que factores como la cercanía a zonas urbanas y turísticas, además de la influencia de las corrientes oceánicas inciden en la variabili= dad estacional y la prevalencia de determinados colores de microplásticos en ecosistemas costeros. Las limpiezas regulares de playas, como la que se rea= liza en Tortuga Bay, pueden reducir la acumulación de estos contaminantes en cie= rtas áreas, lo que sugiere que la intervención humana también puede afectar la distribución y densidad de los microplásticos.

 

Conclusiones

La presencia de microplásticos en la zona costera de Playas Villamil representa un problema ambiental muy grave = que requiere atención. En las muestras recolectadas en esta playa se identifica= ron todos los tipos de microplásticos presentados en las guías (tipo pellet, microfibras, película plástica, fragmento y espuma), sin embargo, el tipo encontrado más frecuentemente en la investigación fue el fragmento y el col= or predominante fue el blanco.

 

En la zona costera de Playas Villami= l se encontraron microplásticos de diferentes tamańos, con rangos que varían ent= re el tamańo máximo de 3 por 22 mm (tipo microfibra) hasta los más pequeńos de= 1 por 1 mm (tipo pellet, microfibras, película plástica y fragmento).

 

Con respecto a la densidad, en el periodo del muestro de noviembre de 2021 a agosto de 2022 se obtuvo un prom= edio de 7.47 unidades de microplásticos por metro cuadrado.

<= span style=3D'font-size:12.0pt;mso-bidi-font-size:11.0pt;font-family:"Arial",san= s-serif'> 

Es probable que= los niveles más altos de microplásticos detectados en las Islas Galápagos comparados con los resultados de este estudio, se deban a que corrientes oceánicas, como la corriente de Humboldt, transportan desechos a las islas. Esto resalta la importancia de estudiar las fuentes y las vías de llegada de los microplásticos para desarrollar estrategias de mitigación.

 

La necesidad de continuar estudiando este tipo de contaminación, ampliando la cobertura geográfica, la periodici= dad y la profundidad, es evidente por la ausencia de estudios previos y lo preocupante de la contaminación por microplásticos a nivel mundial para pod= er tomar medidas preventivas y correctivas. Así mismo, el presente estudio tie= ne un valor especial como punto de partida (línea de base) para futuros estudios.=

=  

= Reconocimiento

 

Queremos expresar nuestro sincero agradecimiento a todos aquellos que contribuyeron a la realización del estu= dio "Identificación y Análisis de Microplásticos en la Zona Costera de Pla= yas (General Villamil), provincia del Guayas, Ecuador", sin su valiosa colaboración y apoyo, este proyecto no habría sido posible.  Investigadores: Teresa Vera San Martín,= Mario Alberto Palacios Moreno, Dolores Isabel Astudillo Brocel, por su liderazgo = en el estudio y el análisis de datos y por la metodología del muestreo y el pr= ocesamiento de las muestras.

 

Equipos de campo y laboratorio: David Segarra Vera, por su dedicación en la recolección de muestras y la asistenc= ia en la toma de datos y monitoreo en la playa, por un buen trabajo en la identificación y el análisis de las muestras en el manejo del laboratorio.<= o:p>

 

Agradecemos a todos los contribuyent= es por el apoyo incondicional y compromiso con la investigación ambiental. Est= ás investigaciones son fundamentales para mejorar el conocimiento de la contaminación por microplásticos en zonas costeras como Playas (G. Villamil= ), y son esenciales para la promoción de prácticas de gestión más sostenibles de= los residuos.

 

 

=  

Re= ferencias <= o:p>

Azoulay 2019. Plastic & Health The Hidden Costs of a Plastic Planet. CIEL Center for Internacional Environmental Law, 8. Obten= ido de https://www.ciel.org/wp-con= tent/uploads/2019/02/Plastic-and-Health-The-Hidden-Costs-of-a-Plastic-Plane= t-February-2019.pdf

Duncan, E.  2019. Diet-related selectivity of macroplastic ingestion in green turtles (Chelonia mydas) in the eastern Mediterranean. 2 - 3. Obtenido de https://www.nature.com/articles/s41598-019-48086-4

EPA’s Microplastic Beach Protocol. <= /span>2021. Guidelines for sampling microplastics on sandy beaches.

Gaibor. 2020. Composición, abundanci= a y fuentes de desechos marinos antropogénicos en las playas de Ecuador - Un estudio apoyado por voluntarios. 2. Obtenido de https://pubmed.ncbi.nlm.nih.gov/32319901/

GESAMP. 2019. Guidelines or the monitoring and assessment of plastic litter and microplastics in the ocean (Kershaw P.J., Turra A. and Galgani F. editors), (IMO/FAO/UNESCO-IOC/UNIDO/WMO/IAEA/UN/UNEP/UNDP/ISA Joint Group of Experts = on the Scientific Aspects of Marine Environmental Protection). Rep. Stud. GESA= MP No. 99, 130p.

Jen S. Jones a, b. A. 2022. Microplastic distribution and composition on two Galapagos ´ island beaches, Ecuador: Verifying the use of citizen science derived data in long-term monitoring.

Leslie, Heather A. Mayo de 2022. Descubrimiento y cuantificación de la contaminación por partículas plástica= s en sangre humana. 6. Obtenido de Descubrimiento y cuantificación de la contaminación por partículas plásticas en sangre humana.: https://www.sciencedirect.com/science/article/pii/S0160412022001258?via%3Di= hub

Mazariegos. 2021. Ocurrencia de microplásticos en el tracto digestivo de peces de la Reserva Natural de Usos Múltiples Monterrico, Guatemala. 3. Obtenido de Ocurrencia de microplástico= s en el tracto digestivo de peces de la Reserva Natural de Usos Múltiples Monterrico, Guatemala: https://www.revistaecosistemas.net/index.php/ecosistemas/article/view= /2188

Moon .2023. Características de los desechos plásticos ingeridos por las tortugas marinas: una revisión exhaustiva. 1. Obtenido de Características de los desechos plásticos ingeridos por las tortugas marinas: una revisión exhaust= iva: = https://www.semanticscholar.org/paper/Characteristics-of-Plastic-Debr= is-Ingested-by-Sea-A-Moon-Shim/fcd507a095502d50b7694ef5fd83232bfccad48b

ONU. 2023. Microplásticos: consecuencias históricas de la contaminación por plásticos. Obtenido de Microplásticos: consecuencias históricas de la contaminación por plásticos: https://www.unep.org/es/noticias-y-reportajes/reportajes/microplasticos-con= secuencias-historicas-de-la-contaminacion-por

Schuyler et al., Q. Mayo de 2014. Identidad equivocada? Similitudes visuales de los desechos marinos con las presas naturales de las tortugas marinas. 2. Obten= ido de Identidad equivocada? Similitudes visuales de los desechos marinos con l= as presas naturales de las tortugas marinas: https://bmcecol.biomedcentral.com/articles/10.1186/1472-6785-14-14

UNEP. 2009. Marine Litter a global challenge. Obtenido de Marine Litter a global challenge: http://hdl.handle.net/20.500.11822/31632<= o:p>

Uhrin, A. V., Hong, S., Burgess= , H. K., Lim, S., & Dettloff, K. 2022. Towards a North Pacific long-term monitoring program for ocean plastic pollution: A systematic review and rec= ommendations for shorelines. Environmental Pollution, 310, 119862.

Wessel, C. C., Lockridge, G. R., Battiste, D., & Cebrian, J. 2016. Abundance and characteristics of microplastics in beach sediments: Insights into micropla= stic accumulation in northern Gulf of Mexico estuaries. Marine Pollution Bulleti= n, 109(1), 178–183. https://doi.org/https://doi.org/10.1016/j.marpolbul.2016.06.002

Williams, A. & Micallef, A. 2009. Beach Management Principles & Practice. London – Sterling : Earthscan.


 

 

 

 

 

 

 

 

 

 

3D"Interfaz
Anexo A.
Material de ayuda para identificación de tipos de microplásticos.

Anexo B. Trabajo en laboratorio con tamices de diferente diám= etro y pasos del trabajo de identificación de microplásticos. a) tamices 1cm;  b) tamices 1 mm ; c) Peso de muestra ; = d) Recipiente de vidrio con agua y sal; e) Identificación de pellets; f,g,h) M= edición de tamańo de plásticos

3D"Cuadro3D"Cuadro   =

3D"Cuadro3D"Cuadro
3D"Una

3D"Cuadro3D"Cuadro3D"Cuadro3D"Cuadro
3D"Una

3D"Cuadro
3D"Una

  =

 

 

 

 

 

Anexo C. = Registro fotográfico de los hallazgos.


= =

=

3D"Interfaz
3D"Forma,
 

 

 

 

 

 

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