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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 =
a>
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=
span>
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.=
span>=
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=
i>
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%. =
p>
=
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=
i>
(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=
span> 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=
span> 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). =
p>
=
=
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=
i>,
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. =
span>
=
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>
<=
span
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