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Quetognatos del Pacifico Ecuatorial y su relación con las variables abióticas durante e= l

Crucero Regional CO-XXVI-2023

 

 

Acta Oceanográfica del Pací= fico

DOI: https://doi org/ 10.54140/raop.v7i1.83<= /p>

Recibido: 05 de agosto, 2024

Aceptado: 20 de enero, 2025

Vol 7. No. 1 2025

ISSN: 1390-129X<= /span>

ISSN: 2806-5522 =

Pg. 1-16<= /p>

 
Chaetognaths from the Equatorial Pacific and <= /p>

their relationship with abiotic variables during the Regional Cruise= CO-XXVI-2023

&= nbsp;

Angie Samaniego

Bióloga

Universidad Estatal Península de Santa Elena

Facultad de Ciencias del Mar

La Libertad – Santa Elena

angiesamaniego20@hotmail.com

ORCID: https://orcid.org/0009-0003-9331-3478

 

Carlos Andrade

<= span lang=3DES style=3D'font-size:9.0pt;font-family:"Arial",sans-serif;mso-farea= st-font-family: Calibri;color:black;mso-color-alt:windowtext;background:white;mso-ansi-lang= uage: ES'>Magister en Ciencias de Manejo Sustentable de Recursos Bioacuáticos

Docente de la Facultad de Ciencias del Mar

Universidad Estatal Península de Santa Elena

La Libertad – Santa Elena

ceandrade@upse.edu.ec

ORCID: http//orcid.org/0000-0001-8804-5956

 

Resumen<= /b>

El zooplancton, compuesto por organismos acuáticos flotantes, juega un papel esencial en la dinámica del ecosistema, reciclando nutrientes y sirviendo de alimento para niveles tróficos superiores. Entre estos organismos, los quetognatos o gusanos flechas se destacan por su naturaleza carnívora y amp= lia distribución, representando hasta un 30% de la biomasa total. Este estudio = tuvo como objetivo evaluar la distribución y abundancia de quetognatos en el mar ecuatoriano durante el Crucero Oceanográfico Regional CO-XXVI-2023. Para el= lo, se monitorearon 14 estaciones ubicadas entre 92°W y 80.5°W, y desde los 1°0= 0’N hasta los 3°00S, mediante arrastres superficiales, identificándose 12 espec= ies de quetognatos. Los análisis estadísticos revelaron una mayor abundancia de organismos en las estaciones E-10, E-20, E-58 y E-59, con densidades de has= ta 1082 ind. (100m³)-1. La especie dominante fue Sagitta enflata (SE), registrando las poblaciones más altas en las E-10 y 57. El índice de diversidad de Shannon & Weaver alcanzó su valor máximo en la = E-17 con 1.9 bits/ind, mientras que el índice de Pielou registró su máxima diversidad de 0.86 bits en la misma estación, sugiriendo= una distribución homogénea de especies. La correlación de Pearson analizó la relación entre la abundancia de especies y los parámetros abióticos, y el análisis de correspondencia canónica (ACC) evidenció los patrones de respue= stas entre las variables ambientales, hidrográficas y las especies de quetognato= s.

Palabras clave: Zooplancton, quetognatos, dinámica del ecosistema, distribución y abundancia.

 =

Abstract

Zooplankto= n, composed of floating aquatic organisms, plays an essential role in ecosystem dynamics by recycling nutrients and serving as food for higher trophic leve= ls. Among these organisms, chaetognaths or arrow worms stand out due to their carnivorous nature and wide distribution, representing up to 30% of the tot= al biomass. This study aimed to evaluate the distribution and abundance of chaetognaths in the Ecuadorian sea during the Regional Oceanographic Cruise CO-XXVI-2023. Fourteen stations located between 92°W and 80.5°W, and from 1°00’N to 3°00’S, were monitored using surface tows, identifying 12 species= of chaetognaths. Statistical analyses revealed a higher abundance of organisms= at E-E10, E20, E58, and E59, with densities of up to 1082 ind. (100m³)-1<= /sup>. The dominant species was Sagitta enflata= (SE), recording the highest populations at E-10 and 57. The Shannon & Weaver diversity index reached its maximum value at E-17 with 1.9 bits/ind, while the Pielou ind= ex recorded its highest diversity of 0.86 bits at the same station, suggesting= a homogeneous distribution of species. Pearson's correlation analyzed the relationship between species abundance and abiotic parameters, and the canonical correspondence analysis (CCA) evidenced response patterns between environmental, hydrographic variables, and chaetognath species.<= /span>

Key words:  Zooplankton, chaetognaths, ecosystem dynamics, distribution and abundance.

 


= Introducción

= El ecosistema del perfil costero ecuatoriano, perteneciente al Pacífico ecuatorial, es de gran importancia económica y social para las comunidades locales. Sin embargo, las variaciones de temperatura superficial del mar y = las actividades antropogénicas han afectado la distribución y la salud del ecosistema, lo que ha llevado a una disminución en la biodiversidad. Los quetognatos, al ser organismos muy sensibles a los cambios ambientales, pue= den ser utilizados como indicadores biológicos de condiciones ambientales en el perfil costero de Ecuador continental y las islas Galápagos.

= El zooplancton, un componente esencial de los ecosistemas acuáticos, desempeña= un papel fundamental en la dinámica y la salud de los ambientes marinos y de a= gua dulce. Para comprender su importancia y su impacto en los ecosistemas, es esencial examinar su definición, estructura y relaciones con otros elementos del medio ambiente. La literatura científica ofrece una variedad de estudios que revelan la complejidad y la relevancia del zooplancton en diferentes contextos y regiones del mundo.

Entre los principales trabajos relacionados a los quetognatos y su relación con las variables ambientales Naranjo, C (2009), = que menciona que las especies S. bipunctata, S. pacifica, S. regularis, Pt= erosagitta draco y Krohnitta pacifica, presentaron correlaciones positivas con los parámetros ambientales tales como temperatura, salinidad y oxígeno disuelto, estas especies podrían ser consideradas como típicas de aguas cálidas oceánicas.<= /span>=

Por otra parte el estudio de las distribución vertica= l y migración vertical de los quetognatos al oeste de las islas Galápagos (Nara= njo, C. 2019), reportó un total de siete especies de quetognatos representados p= or los géneros Sagitta y Krhonitta, con la mayor diversidad se observó en el e= strato entre los 0-40m de profundidad, el cual estuvo influenciado por las corrien= tes marinas principalmente por la Subcorriente Ecua= torial que fue detectada con mayor intensidad hacia el norte de la isla Isabela.=

El propósito de la investigación es recolectar información ambiental y analizar muestras= de zooplancton en diferentes puntos del mar ecuatoriano en un periodo de tiempo corto para establecer las tendencias y evaluar = la distribución y abundancia de los quetognatos y su relación con las variables ambientales = durante el Crucero Oceanográfico Regional CO-XXVI-2023.

= Materiales y Métodos

= Área de Estudio

El área de estudio se circunscribió entre las longitudes 92°W y 80°W hasta latitudes -3°S y 1°N, desarrollado durante el mes de octu= bre 2023. Acorde al track del crucero oceanográfico, se realizaron la toma de muestras en 14 estaciones (Figura 1) que incluyeron estaciones completas, c= on tomas de CTD y de 1000 metros, los muestreos se ubicaron en la sección 92°W, estaciones E5 ubicado a -2°S, E-6 (-1°S), E-10 (0°) y E-11 con 1°N, en la sección 89°W se ubicaron las estaciones E-20 (-1°S) y E-17 ubicada a 1°N, la sección 82°W (E-33, E-44, E-49, E-54, E-57, E-58 y E-59) y sección 80.5°W (E-36). Se <= span style=3D'mso-bookmark:_Hlk173604962'>= establecieron estaciones tanto diurnas de 06:01 a.m. a 06:00 p.m. como nocturnas de 06:01 p.m. a 06: = 00a.m (Tabla 1).


 

Tabla 1= . Coorden= adas de las estaciones analizadas duran= te el crucero regional -1-2023.

Estación

Longitud

Latitud

5

-92

-2

6

-92

-1

10

-92

0

11

-92

1

17

-89

1

20

-88.99

-0.93

33

-82

1

36

-80.5

1

44

-82

-1

49

-82

-2

54

-82

-3

57

-82

-0.5

58

-82

-1.5

59

-82

-2.5

 


= Las muestras superficiales fueron tomadas con una red de plancton con abertura = de malla de 335 micras y un diámetro de boca de red de 30 cm, durante 10 minut= os a una velocidad de 2 a 3 nudos a bordo del Bae Orión.

=  

= Las muestras fueron fijadas en formalina al 4% previamente neutralizado con Bor= áx (Boltovskoy, 1981), las mismas fueron trasladadas al laboratorio para su análisis. El análisis de las muestras e identificación de las especies se realizó en el Laboratorio de Biología del Instituto Oceanográfico y Antárti= co de la Armada del Ecuador (INOCAR) y en los Laboratorios de la UPSE.

= Los análisis cualitativos y cuantitativos del zooplancton se realizaron emplean= do un microscopio y un estereoscopio para contar toda la población de quetogna= tos cuando la muestra era poco abundante. En casos de muestras muy densas, se aplicaron submuestreos utilizando el separador de Folsom (Mc Ewen et al<= /i>., 1954). El número de quetognatos detectados se estandarizó a ind (100m3= )-1.

= La identificación taxonómica de los quetognatos se llevó a cabo a través de la utilización de claves de identificación, Newell G. E. & R. C (1977), IN= OCAR (1983).

= Se emplearon así mismo, las claves de identificación provenientes de diferentes investigaciones para determinar la identidad de los ejemplares adultos. Est= as claves fueron desarrolladas por autores como Sund (1961), Alvariño (1963), Moreno (1973), Boltovskoy y Jankilevich (1981), Bieri, Bonilla & Arcos (1983), Bonilla (1983), Gasca & Suárez (1996), y Ghiardelli (1997).

= Análisis ecológicos estadísticos.

= Se utilizaron índices ecológicos como el Índice de Shannon & Weiner para evaluar la diversidad, el Índice de Simpson para estimar la dominancia y el Índice de Equidad de Pielou para evaluar la uniformidad. Además, se realizó= un análisis de Correspondencia Canónica (ACC) y se empleó el coeficiente de correlación de Pearson para correlacionar la abundancia de las especies con parámetros abióticos.

=  

= Resultados

= Porcentaje de composición por especie (Frecuencia por estación).=

= Se estimaron los porcentajes de composición por especie en las estaciones moni= toreadas utilizando los datos obtenidos individualmente (Figura 2). Cada sección de = las barras representa los diferentes porcentajes observados para cada estación = en los grupos de quetognatos identificados.

En todas las estaciones, = Sagitta enflata (SE) se presentó en por= centajes superiores al 50% en las estaciones E-10, E-11, E-44, E-49, E-54, E-57 y E-= 58, siendo la especie predominante. Sin embargo, su proporción fue menor en las estaciones restantes, excepto en E-36, donde Sagitt= a neglecta (SN) predominó con un 35.7%, y en E-5, donde Krohni= tta subtilis (KS) tuvo un porcentaje similar al= de mayor proporción con un 26.4%.

 =

Sagitta neglecta (S= N) se presentó como la segunda especie en proporción, con porcentajes entre 20% y 35.7% en las estaciones E-5, E-33 y E-36. En las E-6 y E-20, se registraron porcentajes del 17.4% y 19,8%, respectivamente.

 

Sagitta pacifica (SPA) adquirió el terce= r lugar con un 25.3% en la E-33. Las demás especies, incluyendo Sagitta bedoti (SB), Sagitt= a hexaptera (SH), Sag= itta robusta (SRO), Sagitta regularis (SRE), Sagitta pulc= hra (SPU), Sagitta mini= ma (SM), Sagitta bieri= i (SBR) y Sagitta bip= unctata (SBP), presentaron porcentajes inferiores al 15% en todas las estaciones.

 

Densidad y Abundancia por Sección.

 

En la sección 92° W, la E-10 se destaca con una alta densidad de 640 organismo= s, donde Sagitta enflata (SE) domina= con un 83.75%, mientras que Sagitta pulchra (SPU) y Sagitta pacifica (SPA) tienen abundancias mucho menores. En la sección 89° W, la E-20 muestra la mayor abundancia con 708 organismos, y Sagitta enflata (SE) alcanza un 45.20% de dominancia, seguida por Sagitta neglecta (SN) con un 19.77%. En la sección 82° W, la E-44 destaca por su alta densid= ad de 1304 organismos, con Sagitta enfla= ta (SE) representando un 66.87% de la muestra. Finalmente, en la sección 80° W= , la E-36 presenta una densidad de 140 organismos, con S= agitta neglecta (SN) como la especie dominante con= un 35.71%, desplazando a Sagitta enflata= (SE) al segundo lugar con un 34.29%. Estas estaciones ilustran las variacio= nes en la densidad y dominancia de especies clave a lo largo del recorrido del crucero.


=  

=


=  

=  

=  

= En todas las estaciones, Sagitta enflata (SE) se presentó en porcentajes superiores al 50% en las estaciones E-10, E-11, E-44, E-49, E-54, E-57 y E-= 58, siendo la especie predominante. Sin embargo, su proporción fue menor en las estaciones restantes, excepto en E-36, donde Sagitta neglecta (SN) predominó con un 35.7%, y en E-5, donde Krohnitta subtilis (KS) tuvo= un porcentaje similar al de mayor proporción con un 26.4%.

= Sagitta neglecta (SN) se presentó como la segunda especie en proporción, con porcentajes entre 20% y 35.7% en las estaciones E-5, E-33 y E-36. En la= s estaciones E-6 y E-20, se registraron porcentajes del 17,4% y 19.8%, respectivamente.<= o:p>

= Sagitta pacifica (SPA) adquirió el tercer lugar con un 25.3% en la E-33. Las demás especies, incluyendo Sagitta bedoti (SB), Sagitta hexap= tera (SH), Sagitta robusta (SRO), Sagitta regularis (SRE), Sagi= tta pulchra (SPU), Sagitta minima (SM), Sagitta bierii (SBR) = y Sagitta bipunctata (SBP), presentaron porcentajes inferiores al 15% en todas las estaciones.

= Densidad y Abundancia por Sección.

= En la sección 92° W, la E-10 se destaca con una alta densidad de 640 organismos, donde Sagitta enflata (SE) domina con un 83.75%, mientras que Sag= itta pulchra (SPU) y Sagitta pacifica (SPA) tienen abundancias mucho menores. En la sección 89° W, la E-20 muestra la mayor abundancia con 708 organismos, y Sagitta enflata (SE) alcanza un 45.20% de dominancia, seguida por Sagitta neglecta (SN) con un 19.77%. En la sección 82° W= , la E-44 destaca por su alta densidad de 1304 organismos, con Sagitta enflat= a (SE) representando un 66.87% de la muestra. Finalmente, en la sección 80° W= , la E-36 presenta una densidad de 140 organismos, con Sagitta neglecta (= SN) como la especie dominante con un 35.71%, desplazando a Sagitta enflata (SE) al segundo lugar con un 34.29%. Estas estaciones ilustran las variacio= nes en la densidad y dominancia de especies clave a lo largo del recorrido del crucero.

= Distribución de la abundancia/densidad por especie en las estaciones.<= /b>

La distribución de la ab= undancia y densidad por especie muestra una notable variabilidad entre las estacione= s. Sagitta enflata (SE) destaca = por su alta densidad en la E-44 con 1332 ind. (100m3)-1, y también se encuentra en altas densidades en las E-10 (819 ind. (100m3<= /sup>)-1), E-54 (1117 ind. (100m3)-1) y E-57 (1033 ind. (100m3)-1) (Figura 3). Sagitta neglecta (SN) muestra su máxima densidad en la E-20 con 214 ind. (100m3)<= sup>-1, mientras que en otras estaciones sus densidades son mucho menores, como en = la E-59 con solo 12 ind. (100m3)-1. Sagitta pacifica (SPA) alcanz= a su mayor densidad en la E-44 con 168 ind. (100m3)-1, y e= n la E-57 se encuentra a 9 ind. (100m3)-1. En contraste, <= span class=3DSpellE>Sagitta robusta (SRO) present= a una alta densidad en la E-44 con 67 ind. (100m3)-1, pero = es mucho menos frecuente en otras estaciones. Krohnitta subtilis (KS) muestra su máxima densidad en la E-5 con 98 ind. (100m3)-1 y se encuentra a bajas densidades en las E- 6, 58 y 59 con 6 ind. (100m3)-1. Sag= itta pulchra (SPU) tiene su mayor densidad en la E-10 con 61 ind. (100m3)-1, y es baja o inexistente en otras estaciones. Sagitta regularis (SRE) tiene una densidad destacada en la E-44 con 110 ind. (100m3)-1, mientras que en la E-6 su densidad es mínima con 6 ind. (100m3)<= sup>-1. Sag= itta bedoti (SB) tiene la mayor densidad en la E- 20 con 86 ind. (100m3)-1 y no se detecta en varias otras estaciones. Por último, Sagitta minima (SM) presenta su mayor densidad en la E-44 con 34 ind. (100m3)-1, siendo escasa o ausente en muchas estaciones (Tabla 2).



=

 =

Figura 3. Densidad total de Quetognatos por estación.


<= span style=3D'font-family:"Arial",sans-serif;mso-ansi-language:ES-EC'>Índices Ecológicos

 = ;

El análisi= s de los índices de diversidad (H) y equitatividad (J) para la capa superficial = de las estaciones de muestreo muestra una variabilidad significativa. El índic= e de diversidad de Shannon & Weaver (H) alcanzó su valor máximo en la E-17 c= on 1.987 bits/ind (Figura 4), lo que sugiere una alta diversidad y una distribución relativamente uniforme de especies en esa estación. En contras= te, la E-10 presentó el valor mínimo de H, 0.674 bits/ind, indicando una menor diversidad y una distribución de especies menos uniforme. Estaciones adicionales como E-6, E-33, E-20, E-5, E-36 y E-59 también mostraron valore= s de H superiores a 1.5 bits/ind, sugiriendo una diversidad considerable y una distribución casi uniforme de especies. La variación en los índices de diversidad entre estaciones refleja una distribución heterogénea de especie= s a lo largo del área estudiada.

 = ;

El índice = de dominancia reveló que las E-10 y 57 tenían los valores más altos (0.708 y 0= .66, respectivamente), con la especie dominante en estas estaciones siendo Sa= gitta enflata. En contraste, la E-17 tuvo el índice de dominancia más bajo (0.169), lo que indica una mayor equidad entre las especies presentes en esa estación. Estos resultados indican que la dominancia de Sagitta enflata<= /i> varía entre estaciones, sugiriendo una estructura comunitaria diversa y desigual en función de la estación de muestreo.


 =

&n= bsp;

Figura = 4. Índice = de Dominancia-D, Shannon y Equitatividad de Quetognatos.

 = ;

Tabla 2= . Coefici= ente de Correlación (r) entre la abundancia de especies y parámetros abióticos [temperatura (°C), salinidad (UPS), oxígeno (O2), nitrato (NO3), nitrito (N= O2), fosfato (PO4), silicato SiO4) Y pH

 = ;


<= span style=3D'font-family:"Arial",sans-serif;mso-ansi-language:ES-EC'>Coeficient= e de correlación (r) entre abundancia de especies y parámetros abióticos.<= /b>

&= nbsp;

El análisi= s de correlación entre la abundancia de las especies y los parámetros abióticos muestra una variedad de respuestas. Para la especie Krohnitta subtilis, se observaron correlaciones negativas con la temperatura, el nitrato y el p= H, y correlaciones muy débiles con el oxígeno (r =3D 0.180; r² =3D 18%) y otros parámetros como salinidad, nitrito y fosfato. Sagitta bedoti mostró correlaciones negativas significativas con salinidad, oxígeno, nitrato, fos= fato y pH, mientras que las correlaciones positivas para temperatura, nitrito y silicato fueron nulas o muy débiles.

 = ;

<= span style=3D'font-family:"Arial",sans-serif;mso-ansi-language:ES-EC'>Sagitta en= flata mostró correlaciones negativas con la temperatura, nitrato, fosfato y silicato, mientras que las correlaciones positivas con otros parámetros fueron débile= s. Sagitta hexaptera presentó correlaciones negativas fuertes con temperatura (r = =3D -0.601; r² =3D 60.1%), oxígeno (r =3D -0.737; r² =3D 73.7%) y pH (r =3D -0.= 633; r² =3D 63.3%), pero correlaciones positivas significativas con nitrato (r =3D 0.79= 8; r² =3D 79.8%), silicato (r =3D 0.830; r² =3D 83%) y moderadas con fosfato (r = =3D 0.545; r² =3D 54.5%) y salinidad (r =3D 0.534; r² =3D 53.4%). Las correlaciones de Sagitta robusta fueron bajas y negativas para salinidad, nitrato, nitrito y silicato, con correlaciones positivas muy débiles para otros parámetros.

 = ;

Otras espe= cies, como Sagitta regularis, Sagitta pulchra, Sagitta pacifica, Sagitta negle= cta, Sagitta mínima y Sagitta bierii, mostraron una mezcla de correlaciones positivas y negativas, con valores que variaron desde débiles hasta moderados. Por ejemplo, Sagitta bipunctata mostró una fuerte correlación positiva con el nitrito (r =3D 0.840; r² =3D 84%) y correlacion= es negativas para temperatura, fosfato y pH.

&= nbsp;

<= span style=3D'font-family:"Arial",sans-serif;mso-ansi-language:ES-EC'>Análisis de Correspondencia Canónica (ACC).

&= nbsp;

Análisis de Correspondencia Canónica (ACC) reveló que ciertas especies presentan patron= es distintos de respuesta a las variables ambientales. Sagitta enflata y Sagitta robusta están cerca del punto cero en el gráfico de ACC, lo que sugiere que su distribución y abundancia no se ven significativamente afect= adas por las condiciones físicas y químicas del entorno, clasificándolas como cosmopolitas. Sin embargo, Sagitta robusta muestra una influencia específica de los niveles de nitrito.


 = ;

 

Figura 5. Análisis de correspondencia canóni= ca (ACC) de las estaciones monitoreadas con las especies descritas y su relaci= ón con las variables abióticas.


<= span style=3D'font-family:"Arial",sans-serif;mso-ansi-language:ES-EC'> = ;

<= span style=3D'font-family:"Arial",sans-serif;mso-ansi-language:ES-EC'>Sagitta pu= lchra tiene una relación débil con oxígeno, temperatura superficial, nitrato y fosfato, indicando que su densidad poblacional no está estrechamente vinculada a est= os parámetros. El pH y la concentración de oxígeno tampoco parecen afectar significativamente a la distribución de esta especie.

 

En contras= te, las especies Sagitta minima, Sagitta neglecta y Sagitta bipunctata e= stán asociadas con áreas ricas en nitrato, fosfato y silicato, mostrando una relación directa con estos nutrientes. Además, Sagitta pacifica, Sagitta regularis y Sagitta bedoti parecen estar vinculadas a aguas más cálidas= , lo que indica una adaptación a condiciones térmicas específicas.

&= nbsp;

Finalmente= , Sagitta bierii, Sagitta hexaptera y Krohnitta subtilis se encuentran en zonas m= ás frías o en estratos más profundos, posiblemente migrando en respuesta a eve= ntos de afloramiento que aumentan la disponibilidad de nutrientes. El análisis muestra que mientras algunas especies son flexibles y pueden tolerar una variedad de condiciones, otras tienen requerimientos específicos que afecta= n su distribución y abundancia (Figura 5).

 

Discusiones =

 

La distribución y respue= sta de las especies de quetognatos a variables ambientales en el Pacífico ayudan a comprender la ecología marina. Bieri (2003); St= one et al.,(2023), identifican patrones significati= vos en la distribución y adaptación de estas criaturas en su entorno.

 =

Bie= ri (2003), analiza la dist= ribución de 27 especies de quetognatos en el Pacífico, destacando que Sagitta enflata y = Sagitta hexaptera son comunes en aguas ecuatoriales= y centrales, mientras que Sagitta robus= ta y Sagitta pulchr= a prefieren aguas ecuatoriales y centrales occidentales, influenciadas por temperatura, salinidad y oxígeno disuelto.

 =

Stone et al., (20= 23) estudian la influencia de la temperatura y el oxígeno disuelto en la abunda= ncia de quetognatos en North Inlet, encontrando una correlación moderada. También consideran la salinidad y la disponibilidad de nutrientes como factores importantes para especies como Sagitta bipunctata y Sagitt= a mínima.

 =

Naranjo (2009), analizó = la distribución de especies de quetognatos en La Libertad y Manta durante El N= iño 1997-1998, encontrando que especies como Sagitta enflata y S. pacifica dominaban en la capa superficial en marzo = de 1997, asociadas a condiciones oceanográficas específicas.=

 

Durante julio, agosto y = octubre de 1997, se registraron elevadas temperaturas superficiales, coincidiendo c= on la presencia destacada de S. neglecta y = otras especies, sugiriendo una asociación con Aguas Tropicales Subsuperficiales y preferencia por hábitats cálidos.

 =

El estudio subraya la importancia de los patrones de distribución y comportamiento de quetognatos= en relación con condiciones ambientales, relevantes para entender los ecosiste= mas marinos y la respuesta a eventos climáticos como El Niño.=

 =

<= span lang=3DES style=3D'font-family:"Arial",sans-serif'>Conclusiones<= /span>

<= span lang=3DES style=3D'font-size:11.0pt'> 

El análisis de las estac= iones revela que Sagitta enflata es consistentemente la especie más abundante, representando una proporción significativa de la comunidad de organismos en la mayoría de las estaciones= . En estaciones como la E-10 y la E-57, Sagitta enflata supera el 80% de la abundancia total, indicando alta dominancia= y baja diversidad. En contraste, en estaciones como la E-33 y la E-36, la dominancia de Sagitta enflata disminuye, siendo superada o igualada por otras especies como Sagitta pacifica y Sagitta neglecta, sugiriendo variaciones espaciales significativ= as en la estructura de la comunidad de quetognatos. Estos resultados resaltan = una distribución heterogénea de las especies en el área de estudio, influenciada por factores ambientales locales y eventos climáticos que afectan la abunda= ncia y distribución de las diferentes especies.

 =

El análisis de los índic= es ecológicos en la capa superficial muestra una notable variabilidad en la dominancia, diversidad y equitatividad de las especies entre las estaciones= de muestreo. Las E- 10 y 57 presentaron los valores más altos de dominancia, c= on Sagitta enflata como especie dominante, sugiriendo baja diversidad y distribución desigual de especies en estas áre= as. En contraste, la E-17 exhibió el valor más bajo de dominancia y el más alto= de diversidad y equitatividad, indicando alta diversidad y distribución homogé= nea de especies.

 

<= span lang=3DES style=3D'font-family:"Arial",sans-serif'> =

<= span lang=3DES style=3D'font-family:"Arial",sans-serif'>Reconocimiento

<= span lang=3DES style=3D'font-family:"Arial",sans-serif'> =

Deseo expresar mi más si= ncero agradecimiento a los Directivos del Instituto Oceanográfico y Antártico de = la Armada por su invaluable apoyo en proporcionar los datos de nutrientes y en= la culminación de mi trabajo de titulación. Además, agradezco profundamente la oportunidad de participar en el Crucero Oceanográfico Regional CO-XXVI-2023= , lo cual me ha permitido adquirir una experiencia que sin duda fortalecerá mi perfil profesional.

 =

Extiendo también mi grat= itud al Dr. Christian Naranjo Padilla, especialista en Quetognatos, por sus consejo= s en la identificación de este fascinante grupo, especialmente por las valiosas sugerencias emitidas al manuscrito, conocimientos que servirán como referen= cia para las futuras generaciones.

 

<= span lang=3DES style=3D'font-family:"Arial",sans-serif'>Referencias

<= span lang=3DES style=3D'font-family:"Arial",sans-serif'> =

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Samaniego, A. & Andrade C. 2025.                                                 =                             Quetognatos en el Pacífico Ecuatorial

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