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Impacto del dragado de sedimentos= de la laguna de Colta en el hábitat de Chroicocephalus serranus

 

Impact of sedi= ment dredging from the Colta lagoon on the habitat of Chroicocephalus serranus

 


= 1

Javier Ebelio Cargua Inca

 

https://orcid.org/0009-0009-= 3078-1235

 

 

Maestría en Biodiversidad y Cambio Climático, Universidad Península de Santa Elena, Santa Elen= a, Ecuador.

javier.carguainca7625@upse.edu.ec

= 2

Mario Hurtado Domínguez

 

https://orcid.org/0000-0003-1326-2256

 

 

Maestría en Biodiversidad y Cambio Climático, Universidad Península de Santa Elena, Santa Elen= a, Ecuador.

mhurtadodominguez@gmail.com   

 

 

 

 

 

&nbs= p;

 =

 

Artículo de Investigación Científica y Tecnológica

Enviado: 15/03/2024

Revisado: 14/04/2024

Aceptado: 31/05/2024

Publicado:27/06/2024

DOI: https://doi.org/10.33262/= ap.v6i2.2.513        &nbs= p;         

<= span style=3D'font-size:12.0pt;line-height:115%;font-family:"Times New Roman",= serif; mso-fareast-font-family:Calibri;color:blue'> 

 

 

Cítese:

 

 

Carg= ua Inca, J. E., & Hurtado Domínguez, M. (2024). Impacto del draga= do de sedimentos de la laguna de Colta en el hábitat de Chroicocephal= us serranus. AlfaPublicaciones, 6(2.2), 153–165. https://doi.org/10.33262/= ap.v6i2.2.513  

 

 

 

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Palabras claves:

Impacto, contaminación, metales pesados, hábitat, dragado, sedimento, gaviota, laguna

 

Resumen

Introducción: La laguna de Colta ubicada en las parroquias Sicalpa y Santiago de Quito del cantón Co= lta provincia de Chimborazo, cuenta con una extensión de 2.5 km, siend= o el sector donde se realiza la práctica del dragado = de sedimentos en el hábitat de la sp. Chroicocephalus serranus. Metodo= logía: Se elaboró un diagnóstico situacional donde se determinó las actividades antrópicas que se realiza en la laguna y el tipo de dragado que se viene desarrollando; además se procedió a la toma de muestr= as de agua, sedimento y de la especie de ave en tres lugares comprendidos po= r la zona 1: parque Acuático, zona 2: San José y Raya Loma y zon= a 3: Santa Inés posteriormente las muestras fueron enviadas para su respectivo análisis. Objetivos: Se determinó los impactos negativos generados por el dragado de sedimentos de la laguna de Colta en el hábitat de Chr= oicocephalus serranus. Además, se pudo conocer el estado de conservaci&oacu= te;n del hábitat a través de la identificación de los impactos.  Resultados: La presencia de metales pesados como Cu, Ba, Pb, Zn, Fe y Mn con niveles superiores a los admisibles establecidos en las Normas generales de crite= rios de calidad para los usos de las aguas superficiales, marítimas y de estuarios lo cual significa efectos negativos sobre el hábitat de = la gaviota andina (Chroicocephalus serranus). Conclusiones: El análisis de metales pesados de las muestras de sedimento, agua y ave de la laguna revela la existencia de algunos metales pesados tales como: Cu, Pb, Zn, Fe, Mn y Ba. Que pueden resultar tóxicos y perjudícales para la especie. Adem&aacut= e;s, se encontraron alteraciones en los análisis de laboratorio, mismos= que generan impactos negativos en el hábitat de la gaviota andina (Chroicocephalus serranus), generando contaminación química= con metales pesados en los componentes del agua, nutrientes y alimento. &A= acute;rea de estudio general: Ambient= al. Área de estudio específica: Biodiversidad. Tipo de estudio:  Artículos originales.

 

 

Ke= ywords: Impact,

pollution,

heavy metals,

habitat,

dredging,

sediment,

seagull,

lagoon

 

Abstr= act

= Introd= uction: The Colta lagoon located in the Sicalpa and Santiago de Quito parish= es of the Colta canton, province of Chimborazo, has an extension of 2.5 km, being the sector where the practice of sediment dredging is carried out in the habitat of the sp. Chroicocep= halus serranus. Methodology: A situational diagnosis was prepared where the anthropic activities carried= out in the lagoon and the type of dredging that is being developed were determined; In addition, samples of water, sediment and bird species were taken in three places included in zone 1: Aquatic Park, zone 2: San José and Raya Loma and zone 3: Santa Inés. Subsequently, the samples were sent to their respective analysis. Objectives: The negative impacts generated by the dredging of= sediments from the Colta lagoon on the habitat of Chroicocephalus serranus were determined. In addition, the state of conservation of t= he habitat was known through the identification of impacts. Results: The presence of heavy metals such as Cu, Ba, Pb, Zn,= Fe and Mn with levels higher than the admissible levels established in the General Standards of quality criteria for the uses of surface, maritime a= nd estuarine waters, which means effects negative effects on the habitat of = the Andean gull (Chroicocephalus serr= anus). Conclusions: The analysis of= heavy metals from the sediment, water and bird samples from the lagoon reveals = the existence of some heavy metals such as: Cu, Pb, Zn, Fe, Mn and Ba. Which = can be toxic and harmful to the species. In addition, alterations were found = in the laboratory analyses, which generate negative impacts on the habitat of the Andean gull (Chroicocephalus serranus), generating chemical contamina= tion with heavy metals in the components of the water, nutrients and food.

 

 

 

 

Introducción

La laguna de Colta localizada en las parroquias Sicalpa y Santiago de Quito del cantón Colta provincia de Chimborazo, cuenta con una extensión de 2.5 km de largo por 1.1 km de ancho, es uno de los cent= ros turísticos más representativos de la provincia por su trascendencia histórica y cultural (Cruz et = al., 2018). Las diversas actividad= es antrópicas e industriales desarrolladas en el sistema lacustre han desencadenado variados escenarios de contaminación que en el trascur= so del tiempo vienen deteriorando los diversos hábitats (Bocanegra, 2016), con respecto a los siste= mas lacustres tienen una mayor vulnerabilidad debido a que soportan un uso de a= lta intensidad del medio, afectando directamente el proceso de depuración natural (Barrios, 2011). Es por ello por lo que la belleza paisajista d= e la laguna se ha alterado.

Dentro de las amenazas para la laguna es la proliferación de totora, eutrofización y obstrucción de escorrentías, incidiendo de forma directa en el proceso de sedimentación y acumula= ción de sustancias toxicas (Cáceres et al., 2019).

El dragado y la descarga del sedimento extraído puede ser defi= nido como un proceso antrópico inducido de erosión, transporte y almacenamiento de los sedimentos (Bocanegra, 2016). Este proceso tiene un = alto potencial para producir directa o indirectamente impactos negativos en el ambiente de las áreas intervenidas y principalmente en los hábitats de las especies que viven en la laguna de Colta (Landaeta, 2012). Debido a que esta actividad no cuenta con la orientación adecuada y sin tomar en consideración los lineamientos especializados de extracción, = esto ha provocado un considerable impacto ambiental que tiene repercusiones en ámbitos relacionados con la biodiversidad (Landaeta, 2012).

La gaviota andina (Chroicocephalus serranus) es una especie de= ave acuática residente en lagunas y humedales alto andinos de Suramérica; se distribuye desde el sur de Colombia hasta Argentina y Chile. En el territorio ecuatoriano se la encuentra a lo largo del callejón interandino entre los 2.200 m.s.n.m y 4.200 m.s.n.m principalmente en humedales, incluyendo registros esporádicos en la costa y tierras bajas (Nivicela et al., 2023). Considerando que el es= tado de conservación de la sp. es de preocupación menor para el Ecuador según la categoría de la Lista Roja de Especies Amenazadas de la (BirdLife International, 2024).

La presente investigación se enfocó en identificar el impacto del dragado en los sedimentos, agua y ave teniendo como hipótesis que la remoción de los sedimentos provocará = una gran afectación y alteración principalmente en el hábi= tat de la especie Chroicocephalus serranus, ya que es evidente a simple vista que gran cantidad de raíces desprendidas del fondo de la lagun= a se encuentran flotando por distintas zonas que son hábitats de las aves= .

Metodología

En la investigación se manejó el enfoque mixto, porque estuvo integrado por el enfoque cuantitativo y cualitativo. En primera instancia se presentó el enfoque cualitativo orientado al ámbito de biodiversidad con una visión integral = en la relación dragado y hábitat. Posteriormente en la investigación el enfoque tiende a tener un entorno cuantitativo procediendo a realizar el planteamiento de la hipótesis y la presentación de datos.

El diseño fue no experimental de tipo correlacional mediante el método deductivo utilizando las técnicas de observació= n y toma de muestras de agua, sedimento y ave.

Instrumentos: computador, cámara fotográfica, esferos, marcador, hojas, GPS, libreta de campo, aves del Ecuador guía de cam= po, regla, cinta métrica, trampas de red de pesca manual, coolers= , ice pack, preservantes, frascos de vidrio transparente y/o ámbar, frascos de plástico, pisetas, cinta masking, espátula, bolsas plásticas, torunda, jeringa de 1 ml, tubo vial.

Á= ;rea de estudio

En la figura 1, se observa el área de estudio que comprendió la zona del Parque Acuático, sector Santiago de Qu= ito, zona 2 San José y Raya Loma y zona 3 Santa Inés, sectores don= de se desarrolla el dragado y a su vez son depositados los sedimentos.

Figura  SEQ Figura_ \* ARABIC 1

Área de estudio y localización de las= zonas de muestreo

 

 

 

 

 

 

 

 

 

 

 

 

 


Diagnostico situacional

Se realizaron 6 salidas de campo a las zonas de estudio con la finali= dad de elaborar el diagnóstico situacional para identificar las diversas actividades antrópicas que se viene desarrollando en los alrededores= de la laguna y conocer el tipo de dragado que se está aplicando en los sedimentos.

Se recorrió un total de 1.4 km al borde de la laguna, las dos primeras salidas se realizaron en el mes de diciembre del 2023 debido a los altos niveles de extracción de sedimento por el proceso de dragado, = la tercera y cuarta salida se realizó en el mes de febrero para observa= r el traslado del sedimento al área de almacenamiento y finalmente la qui= nta y sexta salida se realizó en el mes de marzo del 2024 para evidencia= r la contaminación generada por el exhaustivo dragado, movilización del sedimento y el traslado de la maquinaria a otra área.=

Recolección de muestras de sedimentos, ag= ua y ave

El material de estudio lo constituyó muestras de agua, sedimen= to de la laguna y dos especies de gaviota andina (Chroicocephalus serranus<= /i>).

Para la recolección de las muestras de agua se utilizó = coolers, ice pack, preservantes, frascos de vidrio transparente y/o ámbar, frascos de plásticos, pisetas y cinta masking, se tomaron 200= ml de agua a una profundidad de 50 cm con los frascos de vidrio previamente tratados con las pisetas, se procedió a rotular con datos referencia= les de la zona de estudio para depositarlos directamente en el cooler ju= nto con el ice pack y los preservantes para su envío al laboratorio en un tiempo menor a 24 horas. Para en análisis bacteriológico del = agua se utilizó la técnica de filtración por membrana al vacío (Agrocalidad, 2018).

Se utilizó una espátula, bolsas plásticas y cint= a masking para la toma de sedimentos, a una profundidad de 10 cm; con la espát= ula se tomó 200 g de muestras que se depositaron en bolsas plásti= cas para ser secados como indica (Parques Nacionales Naturales de Colombia, 2018), y posteriormente se envió al análisis de metales pesa= dos mediante espectrofotometría de absorción atómica.

Para la toma de muestras del ave se procedió a capturar a dos individuos de la sp. utilizando trampas de= red de pesca manual seguidamente se tomó la cabeza del ave entre el dedo medio y el índice y las patas fueron colocadas debajo del codo que n= o se domina para luego ser puestas en una jaula dividida en dos cuadrantes (Hy-Line International, 2016), para la extracción de la sangre se procedió a limpiar la vena braquial con una torunda, posteriormente con una jeringa de 1 ml graduadas de 0 a 100 unidades con aguja calibre 27 y/o 29 G y longitud 13 mm una vez extra&iacut= e;da la muestra se colocó en el tubo vial que contiene solución bu= ffer a base de albuminas y sales, que fueron debidamente codificadas y puestas en una hielera para mantenerla a una temperatura de 2 a 5 ºC (Tully et al., 2016). Para ser transportadas a los laboratorios de la Armada del Ecuador y finalm= ente las aves fueron liberadas en el mismo lugar.

Cabe indicar que tuvimos el acompañamiento de profesionales: un Laboratorista, Zootecnista y un Ornitólogo para cumplir con el protocolo adecuado de la toma de muestras. Además, cada ave fue manipulada manualmente durante 3 min según lo detalla = (Cruz et al., 2018).

Resultados

En los análisis físico-químico realizados a las muestras de agua se identificó la presencia de metal= es pesados tales como: Cu, Pb, Zn, Fe, Mn; mientras que en la de sedimentos se detectaron Cu, Ba, Zn, Fe, Mn y en las muestras de las aves de la especie de gaviota andina se encontraron Cu, Pb, Zn, Fe, Mn siendo algunos de ellos metales pesados tóxicos y perjudiciales para el hábitat de la = especie. Además, en los análisis de agua se evidenció que el pH, color, turbiedad y temperatura se mantienen por debajo de los valores establecidos en la nor= ma de calidad y finalmente el análisis de Coliformes Fecales reveló un valor muy alto de Unidades Formadoras de Colonias sobrepasando el valor permisible.

Tabla 1

Análisis de resultados por contaminación de metales presentes en el agua, sedimento y ave de la laguna de Colta

Parámetro

Resultados muestra 1

Resultados muestra 2

Límites máximos nacionales

Unidad

Agua superficial

Cu

0,013

0,016

0,02

mg/L

Pb

0,225

0,284

 

mg/L

Zn

0,021

0,023

0,18

mg/L

Fe

0,015

0,024

0,3

mg/L

Mn

0,20

0,17

0,1

mg/L

Sedimento Arena superficial

Cu

77,21

50,940

0,02

mg/Kg

Ba

291,63

253,40

1,0

mg/Kg

Zn

5,869

5,324

0,18

mg/Kg

Fe

219,976

180,231

0,3

mg/Kg

Mn

235, 120

190,310

0,1

mg/Kg

Ave

Cu

0,083

0,074

0,02

mg/L

Pb

0,5161

1,010

 

mg/L

Zn

0,11

0,21

0,18

mg/L

Mn

0,2

0,1.15

0,1

mg/L

En la tabla 1, se observa las concentraciones de= los metales pesados encontrados en las muestras de sedimento, agua superficial y especie de gaviota andina Chroicocephalus serranus. Tomando en consideración que el color verde es el valor permisible según= las Normas generales de criterios de calidad (Ministerio del Ambiente, 2015), el color amarillo indica los resultados que no sobrepasan los valores permisibles de la norma= y el color rojo representa los valores que superan los límites permisibles.

Resultados de muestra 1

Muestra de agua: en el análisis de = agua para la muestra 1 se evidencio la presencia de; Pb =3D 0,225 mg/L. Cabe ind= icar que dentro de los valores permisibles para el metal Pb no existe un valor establecido en las Normas generales de criterios de calidad (Ministerio del Ambiente, 2015). Mientras que Cu =3D 0,013 mg/L Zn = =3D 0,021 mg/L; y Fe =3D 0,015 mg/L se mantienen por debajo de los límit= es permisibles y finalmente el metal pesado que sobrepasa los límites de la norma e= s el Mn =3D0,20 mg/L

Muestra de sedimento: en el análisi= s de sedimento se obtuvo los valores de: Cu =3D 77,21 mg/Kg; Ba =3D 291,63 mg/Kg= ; Zn =3D 5,869 mg/Kg; Fe =3D 219,976 mg/Kg y Mn =3D235,120 mg/Kg. Sobrepasando en su totalidad los valores permisibles. &n= bsp;

Muestra ave: se detectó = el metal Zn =3D 0,11 mg/L con un valor que se mantienen por debajo de los límites permisibles mientras que Cu =3D 0,083 mg/L; Pb =3D 0,5161 mg= /L; y Mn =3D0,2 mg/L. sobrepasan los valores permisibles de la norma. 

Resultados muestra 2

Muestra de agua: en el análisis de = agua para la muestra 2 se evidencio la presencia de; Pb =3D 0,284 mg/L. Cabe ind= icar que dentro de los valores permisibles para el metal Pb no existe un valor establecido en las Normas generales de criterios de calidad (Ministerio del Ambiente, 2015). Mientras que Cu = =3D 0,016 mg/L Zn =3D 0,031 mg/L; y Fe =3D 0,024 mg/L se mantienen por debajo d= e los límites permisibles y finalmente el metal pesado que sobrepasa los límites de la norma es el Mn =3D0,17 mg/L.

Muestra de sedimento: en el análisi= s de sedimento se obtuvo los valores de: Cu =3D 50,940 mg/Kg; Ba =3D 253,40 mg/K= g; Zn =3D 5,324 mg/Kg; Fe =3D 180,231 mg/Kg y Mn =3D190,310 mg/Kg. Todos los metales detectados en la muestra sobrepasan los límites permisibles.  

Muestra ave: se encontró= Cu =3D 0,074 mg/L; Pb =3D 1,010 mg/L; Zn =3D 0,21 mg/L y Mn =3D0,1.15 mg/L. Lo= s valores obtenidos sobrepasan los límites permisibles.

Tabla 2

Análisis de características físicas de agua

Parámetros

Unidades

Límites permisibles

Resultados

Ph

 

6-9

8,25

Color

Pt – Co

15

4

Turbiedad

NTU

5

0,21

Temperatura

°C

<40

14,4

Conductividad

μs/cm

-

360,00

En el área de estudio se realizó el análisis de características físicas del agua como se muestra en la tabla 2 donde los parámetros reportaron los siguientes valores: pH =3D 8,25; Color =3D 4 Pt-Co; Turbiedad =3D 0,21 NTU y Temperatu= ra =3D 14,4 °C se mantienen por debajo de los valores establecidos en la norma de calidad y la Conductividad 360,00 μs/cm. 

 

 

 

Tabla 3

Análisis bacteriológico – características físicas

Parámetros

Unidades

Límites permisibles

Resultados

Coliformes fecales

UFC / 100 Ml

1000

1200

Nota: Abrevia= turas: U.F.C Unidades Formadoras de Colonias.

En la tabla 3, se observa el anális= is bacteriológico de Coliformes donde arrojó un resultado de 1200 UFC / 100 mL que supera el valor permisible.

Discusió= ;n

Analizando los resultados obtenidos en esta investigación se puede mencionar que el sistema lacustre de la lagun= a de Colta se encuentra contaminado por la presencia de metales pesados en el ag= ua tales como: Cu, Pb, Zn, Fe y Mn debido a que los sedimentos son removidos d= el fondo y quedan suspendidos en la superficie o en el agua durante y después del dragado y posterior descarga como se menciona en = (Illapa & Betún, 2023).

En las muestras de sedimento se identificó la presencia de Cu, Ba, Zn, Fe y Mn que son metales pesad= os producidos por las actividades humanas como es el caso del dragado <= span lang=3DES-MX style=3D'font-size:12.0pt;line-height:115%;font-family:"Times = New Roman",serif; mso-ansi-language:ES-MX;mso-fareast-language:ZH-CN;mso-bidi-language:SI-LK; mso-no-proof:yes'>(Pulido et al., 2016), que se viene realizand= o en la laguna de Colta con el fin de extraer el sedimento del fondo lacustre pa= ra conservar los espejos de agua.

En la gaviota andina capturada en la zona = de estudio, también se encontró la presencia de metales pesados = como Cu, Pb, Zn y Mn con niveles superiores a los admisibles establecidos en las Normas generales de criterios de calidad para los usos de las aguas superficiales, marítimas y de estuarios (Ministerio del Ambiente, 2015).

El agua presenta alteraciones en sus características químicas, por la presencia de metales pesados= . El agua es considerada como vehículo principal de transporte de contaminantes y el medio donde pueden desarrollar reacciones química= s y físicas, hecho que explica la presencia de estos metales en los sedimentos. Los procesos de dragado y descarga no incorporan nuevos contaminantes al medio acuático: simplemente tienen el potencial para poner en suspensión y distribuir los sedimentos contaminados = (Landaeta, 2012).

Según Armijo= s et al. (2020), los sedimentos, además de ser removidos, h= an sido trasladados y depositados en zonas de acceso directo a la poblaci&oacu= te;n humana como es el caso del parque Acuático. Cabe mencionar que los sedimentos gruesos pueden precipitarse prontamente mientras que los sedimen= tos finos como el limo y la arcilla permanecen en suspensión cubriendo varias áreas de los espejos de agua al ser transportados por las corrientes lacustres y/o por el viento generando turbidez y reduciendo el discernimiento de luz para la fotosíntesis.

Conclus= iones

·      =    El diagnostico situacional identific&oacut= e; las actividades antrópicas en los sitios de investigación de = la laguna, evidenciando la presencia de diversas actividades humanas, como: de= scarga de aguas residuales, intervención de maquinaria pesada, turismo, pes= ca, agricultura y ganadería mismas que podrían estar contribuyend= o a la presencia de metales pesados en estos cuerpos de agua generando impacto = en los ecosistemas acuáticos.

·      =    El análisis de metales pesados en l= as muestras de sedimento, agua y ave de la laguna revela la presencia de algun= os metales pesados tales como: Cu, Pb, Zn, Fe, Mn y Ba. Además, se encontraron alteraciones en los análisis de laboratorio, pará= metros físico-químicos entre los sitios de muestreo, lo que indica u= na variabilidad espacial en la calidad del agua.

·      =    El dragado de sedimentos en la laguna de C= olta genera impactos negativos en el hábitat de la gaviota andina (Chr= oicocephalus serranus), generando contaminación química con metales pesados en los componentes del agua, nutrientes y alimento de la sp. según lo determinan las Normas generales de criterios de calidad para los usos de las aguas superficiales, marítimas y de estuarios.<= /o:p>

= Conflicto de intereses

Los autores declaran que no exist= e conflicto de intereses en relación con el artículo presentado.

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Cáceres del Salto, A. C., Basantes Basantes, E. F., Cocha Telenchana, L. S., & Clavijo Cevallos, M. P. (2019). Evaluación de consorcios fúngicos nativos para biolixiviar los metales pesados bario, vanadi= o y cobre presentes en sedimentos de la laguna de Colta del Cantón Colta. Ciencia Digital, 3(3.4.), 263-275. https://doi.org/10.33262/cienciadigital.v3i3.4.871

Cruz, G., Enriquez, S., & Luzuriaga, N. (2018). Pioj= os (Insecta:phthiraptera) parásitos de la focha andina Fulica Ardesiaca (Gruiformes: Rallidae) en la laguna de Colta, Ecuador. Revista Ecuatori= ana de Ornitología, 3, 6-14. https://doi.org/10.18272/reo.v0i3.520<= o:p>

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Nivicela, M. V. S., Díaz-Fernández, D., Ledesma, L., & Prieto-Albu= ja, F. (2023). Depredación de pichón de focha andina Fulica ardesiaca (RALLIDAE) por la gaviota andina Chroicocephalus serranus (LARID= AE). Revista Ecuatoriana de Ornitología, 9(2), 119-122. https://doi.org/10.18272/reo.v9i2.2813

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Tully, T., Dorrestein, G. M., &a= mp; Jones, A. (2016). Clínica de av= es. Elsevier Editora Ltda. https://books.google.com/books?= id=3DYtCHmVISAKkC&pgis=3D1

Pulido Caraballe, A., Díaz-Asencio, M., Dí= az-Asencio, L., & Alonso Hernández, C. (2016). Evaluación de la contaminación en sedimentos. Centro Azúcar, 43(2), 12= -23. http://scielo.sld.cu/pdf/caz/v43n2/caz02216.pdf

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El artículo= que se publica es de exclusiva responsabilidad de los autores y no necesariamen= te reflejan el pensamiento de la Revi= sta Alfa Publicaciones.

&nb= sp;

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El artículo queda en propiedad de la revista y, por tanto, su publicación parcial y/o total en otro medio tiene que ser autorizado= por el director de la Revista Alfa Publicaciones.

 

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