DOI:

https://doi.org/10.14483/22487638.17675

Publicado:

2022-04-01

Número:

Vol. 26 Núm. 72 (2022): Abril - Junio

Sección:

Investigación

Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon

Factores ambientales, biológicos y pesqueros que influyen en la mortalidad de peces y el desarrollo del evento Cachirra, Laguna Navío Quebrao

Autores/as

Palabras clave:

aclimatación, Cachirra, mortalidad, salinidad, variables (es).

Palabras clave:

acclimatization, Cachirra, mortality, salinity, variables (en).

Biografía del autor/a

Fernando Luis Castro Echavez, Universidad de la Guajira

Licenciado en Biología y Química, especialista en Ciencias Ambientales, Magíster en Ciencias Ambientales, Doctor en Ingeniería Ambiental

Jairo Rafael Rosado Vega, Universidad de la Guajira

Biólogo, Magíster en Ciencias del Mar. Profesor de la Universidad de La Guajira. Director del Grupo de Investigación PICHIHÜEL. Riohacha

Elín Raquel Márquez Gulloso, Universidad de la Guajira

Biólogo, Magíster en Ciencias del Mar. Profesor de la Universidad de La Guajira. Director del Grupo de Investigación PICHIHÜEL

Referencias

Al-Khshali, M. S. (2017). Effect of Salinity on Feed Conversion Rate, Feed Conversion Efficiency, Protein Intake and Efficiency of Protein Utilization Ratio in Common Carp Cyprinus Carpio. American Journal of Life Sciences. Special Issue: Environmental Toxicology, 5(3-1), 30-35. https://www.sciencepublishinggroup.com/journal/paperinfo?journalid=118&doi=10.11648/j.ajls.s.2017050301.15

Alcocer, J. (1997). Biodiversidad y lagos salinos. Biodiversitas, 3(16), 7-14. https://bioteca.biodiversidad.gob.mx/janium/Documentos/1405.pdf

Almeida, P. R. (2003). Feeding ecology of Liza ramada (Risso, 1810) (Pisces, Mugilidae) in a south-western estuary of Portugal. Estuarine, Coastal, and Shelf Science, 57(1-2), 313-323. https://doi.org/10.1016/s0272-7714(02)00357-8 DOI: https://doi.org/10.1016/S0272-7714(02)00357-8

Alonso, A. (2006). Valoración de la degradación ambiental y efectos ecotoxicológicos sobre la comunidad de macroinvertebrados bentónicos en la cabecera del río Henares. Ecosistemas, 5(2), 101-105. https://www.revistaecosistemas.net/index.php/ecosistemas/article/view/512/488

Annichiarico, N. & Guzmán, J. (2006). Diseño de un sistema de monitoreo e implementación de un modelo de simulación de balance hídrico y salinidad de la laguna costera Navío Quebrado, La Guajira colombiana [Undergraduate thesis, Universidad de la Guajira].

APHA, AWWA, & WEF. (2012). Standard methods for the examination of water and wastewater (22nd ed.). American Public Health Association.

Arjonilla, M., & Blasco, J. (2003). Análisis de nutrientes en aguas estuáricas. Efecto de la salinidad. Ciencias Marinas, 29(4), 389-395. https://doi.org/10.7773/cm.v29i4.177 DOI: https://doi.org/10.7773/cm.v29i4.177

Bedoya, C. J. (2004). Caracterización de la pesquería artesanal en la laguna Navío Quebrado. departamento de la Guajira, Caribe Colombiano [Undergraduate thesis, Universidad Jorge Tadeo Lozano]. http://hdl.handle.net/20.500.12010/1359

Botero-Arango, J., & Castaño-Rivera, F. (2005). Inducción de la madurez gonadal del pargo palmero lutjanus analis (pisces: lutjanidae) mediante la aplicación de un fototermoperiodo artificial de acondicionamiento. Boletin de Investigaciones Marinas y Costeras, 34, 69-79. https://doi.org/10.25268/bimc.invemar.2005.34.0.234 DOI: https://doi.org/10.25268/bimc.invemar.2005.34.0.234

Bravo, E., Eslava, N., & González, L. (2009). Crecimiento y mortalidad natural del pez Haemulon aurolineatum (Teleostei: Haemulidae) del suroeste de la isla de Margarita, Venezuela. Revista de Biologia Tropical, 57(3), 699-706. https://doi.org/10.15517/rbt.v57i3.5485 DOI: https://doi.org/10.15517/rbt.v57i3.5485

Bueno, S. E., Marceleño, S., Nájera, O., & De Haro, R. (2019). Implementación del método de escasez en la determinación de la huella hídrica en la zona costera de San Blas, México. Revista Tecnura, 23(62), 45-54. https://doi.org/10.14483/22487638.15796 DOI: https://doi.org/10.14483/22487638.15796

Bustos, D., & Pérez, D. (2003). Ecología trófica y algunos aspectos biológicos de las especies pertenecientes a las familias Mugilidae y Centropomidae en la laguna de Navío Quebrado, Guajira, Caribe colombiano [Undergraduate thesis, Universidad Jorge Tadeo Lozano]. http://hdl.handle.net/20.500.12010/1344

Camargo, J. A., & Alonso, Á. (2006). Ecological and toxicological effects of inorganic nitrogen pollution in aquatic ecosystems: A global assessment. Environment International, 32(6), 831-849. https://doi.org/10.1016/j.envint.2006.05.002 DOI: https://doi.org/10.1016/j.envint.2006.05.002

Canadian Council of Ministers of the Environment (CCME). (2010). Canadian water quality guidelines for the protection of aquatic life: Ammonia. Canadian Environmental Quality Guidelines. https://ccme.ca/en/res/ammonia-en-canadian-water-quality-guidelines-for-the-protection-of-aquatic-life.pdf

Cardona, L. (2001). Non-competitive coexistence between Mediterranean grey mullet: evidence from seasonal changes in food availability, niche breadth and trophic overlap. Journal of Fish Biology, 59(3), 729-744. https://doi.org/10.1111/j.1095-8649.2001.tb02376.x DOI: https://doi.org/10.1111/j.1095-8649.2001.tb02376.x

Castro-Aguirre, J. L. (1982). Los peces de las lagunas Oriental y Occidental, Oaxaca, México y sus relaciones con la temperatura y salinidad. II. Análisis multifactorial. Anales de La Escuela Nacional de Ciencias Biológicas, 26(1-4), 85-100. https://biblat.unam.mx/hevila/AnalesdelaEscuelaNacionaldeCienciasBiologicas/1982/vol26/no1-4/5.pdf

Cervigón, F., & Fischer, W. (1979). Infopesca. Catálogo de especies marinas de interés económico actual o potencial para América Latina. Parte I. Atlántico Centro y Suroccidental (SIC/79/1). FAO/UNDP.

Chasqui-Velasco, L., Polanco, A., Acero, A., Mejía-Falla, P., Navia, A., Zapata L. A., & Caldas, J. P. (Eds). (2017). Libro Rojo de peces marinos de Colombia. Instituto de Investigaciones Marinas y Costeras Invemar, Ministerio de Ambiente y Desarrollo Sostenible.

Chung, M. (2001). Adaptabilidad de una especie eurihalina Oreochromis mossambicus (Peters, 1852) en aguas saladas de la zona nororiental de Venezuela. Revista de Biología Tropical, 49(1). https://www.scielo.sa.cr/scielo.php?script=sci_arttext&pid=S0034-77442001000100002

Cogua, P., Jiménez-Reyes, M. F. & Duque, G. (2013). Relaciones tróficas de cinco especies de peces de interés comercial en la bahía de Cartagena, Caribe colombiano. Boletín de Investigaciones Marinas y Costeras, 42(1), 185-192. https://doi.org/10.25268/bimc.invemar.2013.42.1.68 DOI: https://doi.org/10.25268/bimc.invemar.2013.42.1.68

Costa, L. D. F., Miranda-Filho, K. C., Severo, M. P., & Sampaio, L. A. (2008). Tolerance of juvenile pompano Trachinotus marginatus to acute ammonia and nitrite exposure at different salinity levels. Aquaculture, 285(1-4), 270-272. https://doi.org/10.1016/j.aquaculture.2008.08.017 DOI: https://doi.org/10.1016/j.aquaculture.2008.08.017

Crosetti, D., & Cataudella, S. (1995). Grey mullet culture. In C.E. Nash (Ed.) World Animal Science 34B: Production of Aquatic Animals (pp. 271-288). Elsevier.

de la Lanza-Espino., G. Hernández-Pulido., S., & Gutiérrez-Mendieta., F. J. (2020). Inconvenientes del uso de promedios de parámetros fisicoquímicos no conservativos, ejemplos de caso lagunas costeras mexicanas. Revista Tecnura, 24(65), 85-101. https://doi.org/10.14483/22487638.15973 DOI: https://doi.org/10.14483/22487638.15973

dos Santos, E. D. (1978). Dinâmica de populações aplicada à pesca e piscicultura. Editora Hucitec edusp.

European Environmental Agency (EEA) (2005). Source apportionment of nitrogen and phosphorus inputs into the aquatic. Report No 7. EEA.

Fernández-Delgado, C. Drake, P. Arias, A.M. & García-González, D. (2000). Peces de Doñana y su entorno. Organismo autónomo de parques nacionales. Editorial OAPN.

Franco, L., & Bashirullah, K. M. B. (1992). Alimentación de la lisa (Mugil curema) del Golfo de Cariaco-Estado Sucre, Venezuela. Zootecnia Tropical, 10(2), 219-238. https://baixardoc.com/preview/alimentacion-de-la-lisa-mugil-curema-del-golfo-de-cariaco-estado-suche-venezuela-5cdf1a12193ee

Froese, R. (2006). Cube law, condition factor and weight-length relationships: history, meta-analysis and recommendations. Journal of Applied Ichthyology, 22(4), 241-253. https://doi.org/10.1111/j.1439-0426.2006.00805.x DOI: https://doi.org/10.1111/j.1439-0426.2006.00805.x

Fuentes, F., & Massol-Deyá, A. (2002). Manual de laboratorios: ecología de microorganismos. Editorial Universidad de Puerto Rico.

Gómez-Canchong, P., Manjarrés, L.M., Duarte, L. O., & Altamar, J. (2004). Atlas pesquero del área norte del mar Caribe de Colombia. Universidad del Magdalena.

Guerra, A. & Marín, G. (2002). Algunos aspectos biológicos y pesqueros del lebranche (Mugil liza) en la laguna de Unare, estado Anzoátegui, Venezuela. Zootecnia Tropical, 20(3), 287-305. http://ve.scielo.org/scielo.php?script=sci_arttext&pid=S0798-72692002000300002

Guevara, E., Álvarez, H., Mascaró, M., Rosas, C., & Sánchez, A. (2007). Hábitos alimenticios y ecología trófica del pez Lutjanus griseus (Pisces: Lutjanidae) asociado a la vegetación sumergida en la Laguna de Términos, Campeche, México. Revista de Biología Tropical, 55(3-4), 989-1004. https://doi.org/10.15517/rbt.v55i3-4.5972 DOI: https://doi.org/10.15517/rbt.v55i3-4.5972

Huxley, J. S. (1950). Relative Growth and Form Transformation. Proceedings of the Royal Society B: Biological Sciences, 137(889), 465-469. https://doi.org/10.1098/rspb.1950.0055 DOI: https://doi.org/10.1098/rspb.1950.0055

Instituto de Hidrología, Meteorología y Estudios Ambientales de Colombia. (IDEAM) (2017). Reportes climáticos zona Navío Quebrao 2016-2017. IDEAM.

Molina-Ocampo, R. (1993). Hábitos alimenticios de peces pelágicos menores de importancia comercial del Golfo de California, México [Master's thesis, Instituto Tecnológico de Estudios Superiores de Monterrey].

Molina, A., Duque, G., & Cogua, P. (2020). Influences of environmental conditions in the fish assemblage structure of a tropical estuary. Marine Biodiversity, 50(1), 1-13. https://doi.org/10.1007/s12526-019-01023-0 DOI: https://doi.org/10.1007/s12526-019-01023-0

Nardini, A. (2005). Documentos de modelación matemática para la Laguna Navío Quebrado. Riohacha, La Guajira. Ricerca e Corporazioni.

Negri, S. (2000). Informe Final Ingeniería Hidráulica. Proyecto Prolagunas, Ricerca e Cooperazione..

Oliva-Paterna, F. J., Andreu, A., Minano, P. A., Verdiell, D., Egea, A., de Maya, J. A., Ruiz- Navarro, A., García-Alonso, J., Fernández-Delgado, C., & Torralva, M. (2006). -O-Y fish species richness in the littoral shallows of the meso-saline coastal lagoon (Mar Menor, Mediterranean coast of the Iberian Peninsula). Journal of Applied Ichthyology, 22(3), 235-237. https://doi.org/10.1111/j.1439-0426.2006.00717.x DOI: https://doi.org/10.1111/j.1439-0426.2006.00717.x

Osorio-Dualiby, D. (1985). Ecología trófica de Mugil curema, M. incilis y M. Liza (Pisces: Mugilidae) en la Ciénaga Grande de Santa Marta. [Undergraduate thesis, Universidad Nacional de Colombia].

Osorio-Dualiby, D. (2016). Ecologia trofica de Mugil curema, M. incilis y M. liza (Pisces: Mugilidae) en la Cienaga Grande de Santa Marta, Caribe Colombiano. I. Análisis Cualitativo y Cuantitativo. Boletín de Investigaciones Marinas y Costeras, 18, 446. https://doi.org/10.25268/bimc.invemar.1988.18.0.446 DOI: https://doi.org/10.25268/bimc.invemar.1988.18.0.446

Partridge, G. J., & Jenkins, G. I. (2002). The effect of salinity on growth and survival of juvenile black bream (Acanthopagrus butcheri). Aquaculture, 210(1-4), 219-230. https://doi.org/10.1016/S0044-8486(01)00817-1 DOI: https://doi.org/10.1016/S0044-8486(01)00817-1

Pauly, D. (1984). Fish populations dynamics in tropical waters: a manual for use with programmable calculators. WorldFish.

Pérez, Y. & Ceballos, J. M. (2002). Formulación y validación social de una propuesta de reglamentación en el aprovechamiento artesanal sostenible del recurso camarón (Pennaeus sp.) en el Santuario de Fauna y Flora Los Flamencos, Caribe Colombiano [Undergraduate thesis, Universidad de La Guajira].

Raz-Guzmán, A. (1995). Caracterización trófica de los componentes dominantes de las comunidades bentónicas en Laguna de Términos, Campeche y en la plataforma continental adyacente [Unpublished doctoral thesis, Universidad Autónoma de México].

Ricerca e Cooperazione - Corpoguajira. (2001). Proyecto Prolagunas. Protección y recuperación de humedales costeros del Caribe Colombiano. La Laguna de Navío Quebrado, el ambiente y su gente. Universidad Jorge Tadeo Lozano.

Román, B. (1979). Peces Marinos de Venezuela: claves dicotómicas de los géneros y las especies. Sociedad de Ciencias Naturales La Salle, 39(111-112), 5-408. http://flasa.msinfo.info/portal/bases/biblo/texto/peces_marinos_venezuela.pdf

Romero-Berny, E. I., Velázquez-Velázquez, E., Schmitter-Soto, J. J., & Salgado-Ugarte, I. H. (2020). The influence of habitat on the spatio-temporal dynamics of fish assemblages in a lagoon-estuarine system of the mexican pacific. Latin American Journal of Aquatic Research, 48(1), 23-37. https://doi.org/10.3856/vol48-issue1-fulltext-2349 DOI: https://doi.org/10.3856/vol48-issue1-fulltext-2349

Rosado, J., & Castro-Echavez, F. L. (2011). Comportamiento de las variables fisicoquímicas en los diferentes recursos hídricos del departamento de la Guajira. Editorial Gente Nueva.

Rosado, J., Díaz, L., & Márquez, E. (2011). La Laguna y La Cachirra. Editorial Gente Nueva.

Rosado, J. & Márquez, E. (2004). Efectos climáticos y fisicoquímicos sobre la formación y mortalidad de Cachirra, Laguna Navío Quebrao, LNQ, Camarones [Conference presentation]. VI seminario internacional de Limnología, Monteria, Colombia.

Rosado, J., & Cortés, L. (2006). Aspectos florísticos y ecológicos de la Laguna Navío Quebrao, Camarones, Riohacha, La Guajira, Colombia. Ciencia e Ingeniería Aplicada, 1, 9-21.

Rosas-Luis, R., Andrade, P., Avila-Tumbaco, A., & Pincay-Espinoza, J. (2016). Manual para la identificación de peces óseos marino-costeros del Pacífico ecuatoriano basado en esqueletos axiales. Manta, Manabí, Ecuador. Editorial Mar abierto.

Ruiz, J.A. & Ramírez, J. G. (2002). Valoraciones preliminares de los principales componentes bióticos y fisicoquímicos en la Laguna Navío Quebrao (Guajira, Colombia): Informe final. Ricerca e Cooperazione – European Union – Corpoguajira.

Sánchez-Hernández, J. Servia, M. Vieira-Lanero, R. & Cobo, F. (2010). Evaluación del lavado gástrico como herramienta para el análisis de la dieta en trucha común. Limnetica, 29(2), 369-378. https://doi.org/10.23818/limn.29.30 DOI: https://doi.org/10.23818/limn.29.30

Schofield, P. J., Peterson, M. S., Lowe, M. R., Brown-Peterson, N. J., & Slack, W. T. (2011). Survival, growth and reproduction of non-indigenous Nile tilapia, Oreochromis niloticus (Linnaeus 1758). I. Physiological capabilities in various temperatures and salinities. Marine and Freshwater Research, 62(5), 439-449. https://doi.org/10.1071/MF10207 DOI: https://doi.org/10.1071/MF10207

SENA & Ministerio de Ambiente y Desarrollo Sostenible. (1998). Diagnóstico rural rápido, Santuario de Fauna y Flora los Flamencos, corregimiento de Camarones, Riohacha. SENA, MADS.

Serrano, X., Serafy, J., & Grosell, M. (2011). Osmoregulatory capabilities of the gray snapper, lutjanus griseus: Salinity challenges and field observations. Marine and Freshwater Behaviour and Physiology, 44(3), 185-196. https://doi.org/10.1080/10236244.2011.585745 DOI: https://doi.org/10.1080/10236244.2011.585745

Shikano, T., Chiyokubo, T., & Taniguchi, N. (2001). Effect of inbreeding on salinity tolerance in the guppy (Poecilia reticulata). Aquaculture, 202(1-2), 45-55. https://doi.org/10.1016/S0044-8486(01)00568-3 DOI: https://doi.org/10.1016/S0044-8486(01)00568-3

Simier, M., Blanc, L., Aliaume, C., Diouf, P.S., & Albaret, J. J. (2004). Spatial and temporal structure of fish assemblages in an “inverse estuary”, the Sine Saloum system (Senegal). Estuarine, Coastal and Shelf Science, 59(1), 69-86. https://doi.org/10.1016/j.ecss.2003.08.002 DOI: https://doi.org/10.1016/j.ecss.2003.08.002

Smyth, K., & Elliott, M. (2016). Effects of changing salinity on the ecology of the marine environment. In M. Solan & N. Whiteley (Eds.), Stressors in the Marine Environment. Physiological and ecological responses; societal implications (pp. 161-174). Oxford University Press. https://doi.org/10.1093/acprof:oso/9780198718826.003.0009 DOI: https://doi.org/10.1093/acprof:oso/9780198718826.003.0009

Stone, D. A. J., Roberts, S. D., & Krishna-Lee, C. (2014). Hyper-Saline Conditions Affect Growth, Osmoregulation and Survival of Fingerling and Juvenile Yellowtail Kingfish. Seriola Lalandi. Journal of Aquaculture and Marine Biology, 1(1), 19-27. https://doi.org/10.15406/jamb.2014.01.00005 DOI: https://doi.org/10.15406/jamb.2014.01.00005

Strydom, N. A. (2003). Occurrence of larval and early juveniles fishes in the surf zone adjacent to two intermittently open estuaries, South Africa. Environmental Biology of Fishes, 66(4), 349-359. https://doi.org/10.1023/a:1023949607821 DOI: https://doi.org/10.1023/A:1023949607821

Cómo citar

APA

Castro Echavez, F. L., Rosado Vega, J. R., y Márquez Gulloso, E. R. (2022). Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon. Tecnura, 26(72), 17–41. https://doi.org/10.14483/22487638.17675

ACM

[1]
Castro Echavez, F.L., Rosado Vega, J.R. y Márquez Gulloso, E.R. 2022. Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon. Tecnura. 26, 72 (abr. 2022), 17–41. DOI:https://doi.org/10.14483/22487638.17675.

ACS

(1)
Castro Echavez, F. L.; Rosado Vega, J. R.; Márquez Gulloso, E. R. Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon. Tecnura 2022, 26, 17-41.

ABNT

CASTRO ECHAVEZ, F. L.; ROSADO VEGA, J. R.; MÁRQUEZ GULLOSO, E. R. Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon. Tecnura, [S. l.], v. 26, n. 72, p. 17–41, 2022. DOI: 10.14483/22487638.17675. Disponível em: https://revistas.udistrital.edu.co/index.php/Tecnura/article/view/17675. Acesso em: 27 ene. 2023.

Chicago

Castro Echavez, Fernando Luis, Jairo Rafael Rosado Vega, y Elín Raquel Márquez Gulloso. 2022. «Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon». Tecnura 26 (72):17-41. https://doi.org/10.14483/22487638.17675.

Harvard

Castro Echavez, F. L., Rosado Vega, J. R. y Márquez Gulloso, E. R. (2022) «Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon», Tecnura, 26(72), pp. 17–41. doi: 10.14483/22487638.17675.

IEEE

[1]
F. L. Castro Echavez, J. R. Rosado Vega, y E. R. Márquez Gulloso, «Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon», Tecnura, vol. 26, n.º 72, pp. 17–41, abr. 2022.

MLA

Castro Echavez, F. L., J. R. Rosado Vega, y E. R. Márquez Gulloso. «Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon». Tecnura, vol. 26, n.º 72, abril de 2022, pp. 17-41, doi:10.14483/22487638.17675.

Turabian

Castro Echavez, Fernando Luis, Jairo Rafael Rosado Vega, y Elín Raquel Márquez Gulloso. «Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon». Tecnura 26, no. 72 (abril 1, 2022): 17–41. Accedido enero 27, 2023. https://revistas.udistrital.edu.co/index.php/Tecnura/article/view/17675.

Vancouver

1.
Castro Echavez FL, Rosado Vega JR, Márquez Gulloso ER. Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon. Tecnura [Internet]. 1 de abril de 2022 [citado 27 de enero de 2023];26(72):17-41. Disponible en: https://revistas.udistrital.edu.co/index.php/Tecnura/article/view/17675

Descargar cita

Visitas

9

Dimensions


PlumX


Descargas

Los datos de descargas todavía no están disponibles.

Recibido: 1 de marzo de 2021; Aceptado: 7 de febrero de 2022

ABSTRACT

Context:

The Navío Quebrao lagoon (NQL) has always played an important role in the economy of the indigenous communities in its surroundings. However, in recent years, the tributaries to the lagoon have been notably impacted by climatic variability and logging activities, therefore clogging the lagoon and causing the loss of depth, which increases the temperature and salinity. In three months, 80% of the lagoon dries out, causing the mortality of most of the species inhabiting it. This phenomenon is known as the Cachirra event. Therefore, this study aims to analyze the incidence of environmental, biological, amd fishing factors in the formation and mortality of the Cachirra event..

Methodology:

We collected samples from fishing nets used by the fishermen of the arranchaderos community. IDEAM provided 2017 climatologic data. Physicochemical variables were measured with a Spectroquant SQ 118 and other direct measurement electronic devices. The R statistical software version 3.2.2 was used to analyze the data and their relationships.

Results:

The results showed that 12 species are involved in the formation of the Cachirra event, predominantly the Mugilidae family. Salinity was the physicochemical variable that predominantly affected the mortality of the species -October (6,0 ± 0,6 UPS) and March (67,4 ± 1,36 UPS).

Conclusions:

Fish die according to their susceptibility to salinity changes, with Cathrorops spixii and Eugerres plumieri being the most susceptible species and Elops saurus and Mugil liza the most resistant. The species present in the NQL have lengths well below commercial significance and different condition factor and repletion index values before and after the Cachirra event.

Funding:

Universidad de La Guajira

Keywords:

acclimatization, Cachirra, mortality, salinity, variables.

RESUMEN

Contexto:

La laguna Navío Quebrao (NQL) siempre ha jugado un papel importante en la economía de las comunidades indígenas que se encuentran a su alrededor. Sin embargo, en los últimos años, sus tributarios han sido impactados notablemente por la variabilidad climática y la actividad de tala, trayendo como consecuencia la colmatación de la laguna y causando la pérdida de profundidad, lo cual aumenta la temperatura y la salinidad. En 3 meses se seca el 80 % de la laguna, lo cual causa la mortalidad de la mayoría de las especies que la habitan. Este fenómeno es conocido como evento Cachirra. Por lo tanto, este estudio pretende analizar la incidencia de factores ambientales, biológicos y pesqueros en la formación y mortalidad del evento Cachirra.

Metodología:

Recolectamos muestras de las redes de pesca utilizadas por los pescadores de la comunidad de arranchaderos. El IDEAM proporcionó datos climatológicos de 2017. Las variables fisicoquímicas se midieron con un Spectroquant SQ 118 y otros dispositivos electrónicos de medición directa. Se utilizó el software estadístico R versión 3.2.2 para analizar los datos y sus relaciones.

Resultados:

Los resultados muestran que 12 especies están involucradas en la formación del evento Cachirra, predominantemente la familia Mugilidae. La salinidad fue la variable fisicoquímica que más afectó la mortalidad de la especie -octubre (6,0 ± 0,6 UPS) y marzo (67,4 ± 1,36 UPS).

Conclusiones:

Los peces mueren según su susceptibilidad a los cambios de salinidad, siendo las especies más susceptibles Cathrorops spixii y Eugerres plumieri y las más resistentes Elops saurus y Mugil liza. Las especies presentes en la NQL tienen longitudes muy por debajo de la importancia comercial y diferentes valores de factores de condición y del índice de repleción antes y después del evento Cachirra.

Financiamiento:

Universidad de La Guajira

Palabras clave:

aclimatación, Cachirra, mortalidad, salinidad, variables.

INTRODUCTION

The Navío Quebrao Lagoon (NQL) is a relevant body of water because it is part of the Flamingos Flora and Fauna Sanctuary (SFFF). The sanctuary was established for the protection of the pink flamingo (Phoenicopterus ruber, Linnaeus, 1758). The lagoon also serves as economic support for the fishing communities, mostly indigenous people settled in its surrounding areas. The NQL experiences physiographic and biodynamic changes from October to March, leading to variations in hydrology and water physicochemical variables (Ricerca e Coorperazione - Corpoguajira, 2001). Cachirra (a word given by the natives of the area) is an event consisting of the massive mortality of juvenile fish inhabiting the lagoon, which results from changes during a low precipitation season. These changes lead to a progressive increase in salinity and a reduction of food availability, as indicated by de la Lanza-Espino et al. (2020). The authors mention that the variations in the coastal physicochemical and biological parameters are the result, among others, of natural factors such as climate.

The Cachirra event negatively impacts the economy of the indigenous people living in the area (Rosado et al., 2011) because the species involved in this event, specifically the mugilids, do not reach the commercially required sizes to be well valued in the market. This affects the potential revenues for the local fishermen. The constant opening of the river mouth to allow the influx of water, which is instrumental to the growth of the species, is restricted by the community. This situation creates a dilemma that should be tackled in order to encourage the ancestral culture of the Cachirra event, given that it is part of the cultural identity of the people living in the area.

Numerous studies in NQL have focused on the fields of hydrology and hydrodynamics (Negri, 2000); hydrodynamic, climatic, biological, and socioeconomic aspects (Ricerca e Cooperazione - Corpouajira, 2001; Ruiz & Ramírez, 2002); regulation of artisanal use (Pérez, & Ceballos, 2002); floristic and ecological aspects (Rosado & Cortés, 2006); physicochemical variables and phytoplankton population (Rosado & Márquez, 2004); mathematical modeling (Annichiarico & Guzmán, 2006; Nardini, 2005); and artisanal fishery (Bedoya, 2004). Several studies assess the impact of salinity and temperature on growth (Shikano et al., 2001). The increased salinity negatively affects the feed conversion rate and efficiency, the protein intake, and the efficiency of protein utilization (Al-Khshali, 2017; Schofield et al., 2011).

In general, Mugilidae species have a high ecological plasticity. Mugilids are able to consume a variety of foods: detritus (which they can also filter out), algae, crustaceans, mollusks, insects, and large amounts of silt from the bottom (Cardona, 2001; Fernández-Delgado, et al., 2000). These features make them an ecologically important family due to its decisive contribution to the energy and matter flow from the lower to the upper levels of the ecosystems they inhabit (Almeida, 2003). Several mugilid species can inhabit the same estuary, as they utilize the food distributed from the thin water surface film to the bottom mud, either by direct grazing or using plant-detritus food chains as an energy source (Crosetti & Cataudella, 1995). Due to this, Mugilidae is always one of the dominant fish families in the ecosystems it inhabits (Oliva-Paterna et al., 2006; Simier et al., 2004; Strydom, 2003). The majority of Mugilidae species are highly euryhaline (Cardona, 2001).

This study aims to generate basic information on the behavior of the most relevant aspects regarding the environmental and biological factors that affect the dynamics of the NQL. It also aims to identify the relevant variables causing the massive fish mortality during the Cachirra event. The findings of this study could be used by provincial government agencies to design comprehensive policies and strategies that may lead to short-term mitigation of fish mortality and to reduce crustacean and mollusk presence in the lagoon. According to a study by Negri (2000) about the environmental impacts on the hydrological and hydrodynamics of the lagoon, the logging of forests in the main tributary channel and sand extraction activities were found to have a major impact. The research concluded that, within 20 years, the NQL would be completely clogged. Therefore, local authorities need to regulate these activities and must implement strategies to preserve the formation of the Cachirra event since it influences the cultural identity of the people living in the area. At the same time, the preservation of the event allows crustaceans to reach a larger size, thus improving their commercial value and the subsequent increase in the income of the indigenous people and afro-descendant communities living in the surroundings of the lagoon.

METHODOLOGY

Study area

The area under study is called Navío Quebrao Lagoon or Camarones lagoon, and it is located in the Northwest of the department of La Guajira, in the municipality of Riohacha (11° 27'-11° 22' North and 73° 11'-73° 7 ' West). It is at an altitude of 5 masl and has a maximum flood surface of 9 km2, approximately 900 ha (Figure 1).

The study area of the NQL with the sampling stations

Figure 1: The study area of the NQL with the sampling stations

Source: Authors

Methods

Research activities were conducted from October 2016 to March 2017. They covered the wet season (October, November, and December) and the dry season (January, February, and March). Climatological, biological, and physicochemical variables, as well as the sequence of fish mortality by species were measured again in 2018. The average values were used for variable analysis. In the wet season, three sampling stations were designated. A sampling station known as S1 was located 100 m from the mouth of the Camarones river. The S2 site was located 100 m from Arroyo de Los Indios and S3 at the center of the lagoon. In the dry season, there is a displacement and a significant reduction of the lagoon area to approximately 5 ha on the western side of the lagoon. The water column also decreases, maintaining a uniform depth during drought time. Thus, only one sampling station was established (S3) at the center of the lagoon.

The main changes or disturbances occur at the entrance of Arroyo Camarones [Camarones Stream], which correspond to S1; the others correspond to the mouth of the lagoon (S2). No additional sampling stations were installed, since the other areas are dead spots where the variables do not show any alteration that is relevant for the study. The location of the S3 station was selected considering that the evaporation process starting in December causes S1 and S2 to disappear, thus reducing the water area to approximately 50 ha in the western sector, where S3 is located. It is important to mention that there are no major industries or roads in the area. There are only some small houses belonging to indigenous communities who are very isolated from each other, and they have no impact on the dynamics of the lagoon.

Climatological and physicochemical variables

Data corresponding to climatological variables (maximum temperature, minimum temperature, average temperature, relative humidity, sunshine, maximum wind, wind speed, precipitation, evaporation, and cloudiness) were provided by IDEAM (2017). A WTW 3320 Multiparameter was utilized to perform in situ monitoring (in triplicate) of physicochemical variables (salinity; potential of Hydrogen, pH; dissolved oxygen, DO; and water temperature). Turbidity was measured with a HACH 2100P turbidimeter. Samples were collected in triplicate in 500 mL polyethylene bottles to determine (ex-situ) the concentrations of nitrites and ammonium. They were then transported and kept at 4 ºC to be analyzed at the Environmental Quality Laboratory of Universidad de La Guajira within 8 hours of their collection (APHA, AWWA, & WEF, 2012). Following Camargo and Alonso's (2006) recommendations, we selected five variables due to the lethal effects they can have on fish survival: temperature, dissolved oxygen, nitrites, pH, and ammonium.

The standardized methods (APHA, AWWA & WEF, 2012) used for the analysis of the physicochemical variables are indicated in Table 1.

Table 1: Variables, methods, and equipment for physicochemical analysis

VARIABLE ANALYTICAL METHODS EQUIPMENT
In-situ physicochemical analysis
Water temperature (ºC) Thermometric (Method 2550 B) WTW 3320 Multiparameter
pH (Unit) Electrometric (Method 4500 H+B) WTW 3320 Multiparameter
Salinity (PSU) Electrometric (Method 2520 B) WTW 3320 Multiparameter
Dissolved oxygen (mg/L) Membrane-Electrode. (Method 4500 - O G) WTW 3320 Multiparameter
Ex-situ physicochemical analysis
Nitrite (mg/L) Photometric (Analogous to Method 4500- NO 2 − B) Spectroquant model SQ 118 (Merck brand)
Ammonium (mg/L) Photometric (Analogous to Method 4500-NH3 D) Spectroquant model SQ 118 (Merck brand)

Source: Authors, based on APHA, AWWA & WEF (2012)

Inventory of fish species, biometric parameters, and stomach contents

For the identification of the species, previous knowledge and the existing specialized bibliography were used (Cervigón & Fischer, 1979; Chasqui-Velasco et al., 2017; Román, 1979; Rosas-Luis et al., 2016) after weekly manual randomized sampling of moribund floating fish species throughout the lagoon. We recorded the sequence of fish mortality for the species involved in the Cachirra event. Samples were also taken from arranchaderos, places where fish are laid in the open for sun-drying, following their collection with different fishing equipment such as cast nets, trammels, and manuals (Rosado et al., 2011; Ruiz & Ramírez, 2002).

We measured the total length (TL) of the fish with an ichthyometer (a fish measuring board) and the weight (W) with a balance in order to compare the commercial size to the size and weight of the species of the Cachirra event. The length-weight relationship of the species was determined using the allometric growth formula W = a*Lb (Froese, 2006; Huxley, 1950) and linearized by means of a logarithmic transformation. The state of gastric repletion (SGR) and food content were determined using a randomized sample of 50 individuals for each species. Their stomachs were extracted, and their content was preserved in 10% formaldehyde and analyzed with a Nikon E400 stereoscope (Sánchez-Hernández et al., 2010). The Repletion index (RI) was calculated with Equation (1) (dos Santos, 1978; Molina-Ocampo, 1993):

Taxonomic classification of animal samples was conducted only for the upper categories, namely insects, crustaceans, nematodes, and polychaetes. The rest of the samples were classified as detritus, filamentous algae, microalgae, and sand. Following Pauly (1984), the condition factor (CF) was used to determine the relationships between feeding and fish growth during the various stages of development. Equation (2) was used to obtain this factor:

The species involved in the Cachirra event were determined through a survey that inquired fishers for the species that they considered to be components of the event. The identified species were those with greater acceptance and demand in the market, as well as those prefferred by the community due to their flavorful taste, which is acquired during the salting and sun-drying process.

Mortality sequence in component species of the Cachirra event

The dry season began in December 2016 and lasted until February 2017. Constant observations were made of the body of water, and, if fish mortality was observed in the area, then the species were collected and measured. The salinity and the salinity range that caused the death of the species were determined using the WTW 3320 Multiparameter.

Statistical analysis

For the analysis and interpretation of the physicochemical and climatic results, the initial data were transformed into a correlation matrix by applying Pearson's product-moment correlation coefficient between pairs of physicochemical and climatic variables using the R statistical package, version 3.2.2. In order to search for associations between the studied variables, a cluster analysis was performed using Ward's algorithm and the similarity matrix based on the Bray Curtis Index. The evaluation of significant differences in the temporal behavior of all the physicochemical variables during the study was carried out by means of the non-parametric Wilcoxon test with a significance level of 0,05.

RESULTS

Climatic variables

Table 2 reports climatic variable data corresponding to the wet months (October, November, and December 2016) and the low water level period (January, February, and March 2017). We observed variations in the records of precipitation, cloudiness, wind speed, and evaporation during the wet and dry seasons, which affected the biodynamics of the lagoon.

Table 2: Record of the main climatic variables in the Navío Quebrao Lagoon

Variables Units Rainy season (2016) Drought time (2017)
Oct. Nov. Dec. Jan. Feb. Mar.
Maximum temperature °C 36,9 34,7 34,6 34,7 36,1 36,4
Minimum temperature °C 22,4 20,8 21,7 19,8 19,2 18,9
Average temperature °C 28,4 27,7 27,8 28,0 27,0 27,5
Relative humidity % 78,0 80,0 75,0 63,0 64,0 66,0
Solar brightness h/sun 217,8 194,5 228,7 278,7 242,8 231,7
Maximum wind km/h 42,0 39,0 46,0 65,0 68,0 62,0
Wind speed m/s 2,8 2,4 2,7 2,8 4,9 4,3
Precipitation mm 126,4 138,6 14,9 1,9 0,0 0,0
Evaporation mm/day 6,2 4,6 6,1 7,6 7,9 8,3
Cloudiness Octas 7/8 6/8 5/8 4/8 3/8 2/8

Source: Authors, based on IDEAM (2016, 2017)

Physicochemical variables

Table 3 shows the behavior of the physicochemical variables during the wet and dry seasons, as well as the variations in salinity experienced from October (6,0 ± 0,6 PSU) to March (67,4 ± 1,36 PSU).

Table 3: Average records of physicochemical variables in the months of rain and drought

Variables Units N Rainy season (2016) Drought time (2017)
Oct. Nov. Dec. Jan. Feb. Mar.
Salinity PSU 3 6,0 ± 0,6 23,0 ± 2,64 33,6 ± 1,24 35,0 ± 0,36 41,5 ± 1,41 67,4 ± 1,36
pH Unit 3 8,0 ± 0,2 7,9 ± 0,3 7,9 ± 0,26 8,5 ± 0,17 8,1 ± 0,2 8,2 ± 0,26
Dissolved oxygen mg/L 3 5,2 ± 0,4 5,6 ± 0,43 5,4 ± 0,3 5,2 ± 0,1 5,1 ± 0,36 4,4 ± 0,52
Water temperature °C 3 29,0 ± 0,91 28,0 ± 0,91 28,0 ± 0,62 26,0 ± 0,70 26,0 ± 0,36 28,0 ± 0,52
Nitrite mg/L 3 0,40 ± 0,04 0,50 ± 0,09 0,40 ± 0,1 0,01 ± 0,01 0,01 ± 0,01 0,01 ± 0,01
Ammonium mg/L 3 0,20 ± 0,02 0,50 ± 0,04 0,50 ± 0,05 1,00 ± 0,2 1,00 ± 0,1 1,00 ± 0,17

Source: Authors

Species inventory

Table 4 indicates the presence of 34 species comprised by 20 families, mostly of marine and estuarine origin. We observed four genera belonging to Carangidae and Penaeidae families (11,8%); three genera belonging to Gerreidae and Mugilidae (8,8%); and one genus for each of the following families: Belonidae, Clupeidae, Dasyatidae, Gobiidae, Poeciliidae, and Pomacanthidae (2,9%). Fishermen of the area have linked the Cachirra event to twelve species out of the 34 species found. That is 35,3% of the total number of species living in the lagoon. Cachirra species are members of seven families, which is 35,0% of the total families in the lagoon.

Table 4: Reported species and components of the Cachirra event

Family Scientific name
Ariidae * Bagre Marinus Mitchill
* Cathorops spixii Agassiz
Belonidae Strongylura marina Walbaum
Bothidae Citharichthys spilopterus Günther
Carangidae Chloroscombrus chrysurus L.
* Caranx hippos L.
Oligoplites saurus Bloch & Schneider
* Trachinotus falcatus L.
Centropomidae * Centropomus ensiferus Poey
Centropomus undecimalis Bloch
Clupeidae Harengula clupeola Cuvier
Dasyatidae Dasyatis guttata Bloch & Schneider
Elopidae * Elops saurus L.
Engraulidae Anchovia clupeoides Swainson
Gerreidae * Diapterus rhombeus Cuvier
Eucinostomus argenteus Baird & Girard
* Eugerres plumieri Cuvier
Gobiidae Gobioides broussonneti Lacepède
Lutjanidae Lutjanus griseus L.
Megalopidae Tarpon atlanticus Cuvier & Valenciennes
Mugilidae * Mugil curema Valenciennes
* Mugil incilis Hancock
* Mugil liza Valenciennes
Palaemonidae Macrobrachium acanthurus Wiegmann
Macrobrachium carcinus L.
Penaeidae Penaeus notialis Perez
Penaeus schmitti Burkenroad
Penaeus subtilis Perez
Xiphopenaeus kroyeri Heller
Poeciliidae Poecilia vivipara Bloch & Schneider
Pomacanthidae Pomacanthus paru Bloch
Portunidae Callinectes bocourti Milne
Callinectes sapidus Rathbun
Sciaenidae * Micropogonia furnieri Desmarest
* Cachirra component species

Source: Authots

Mortality sequence in species involved in the Cachirra event

Table 5 shows the sequential order of deaths for the 12 Cachirra species. The species most susceptible to salinity were C. spixii and B. marinus, with values ranging between 45 and 50 PSU. The most resistant were M. liza and E. saurus, which died when the salinity exceeded 70,0 PSU.

Table 5: Sequential order of mortality in the component species of the Cachirra event

UPS=45-50 50-55 55-60 60-65 >64,7
C. spixii D. rhombeus C. hippos T. falcatus M. curema M. liza E. saurus
B. marinus E. plumieri C. ensiferus M. furnieri M. incilis

Source: Authors

Parametric variables

M. incilis had the highest number of captures during fishing days (584 fish), followed by M. liza (204 fish). B values were close to 3,0. C. spixii reached the highest value (2,9730). r 2 values were above 0,8, with the highest value (0,9354) corresponding to C. spixii (Table 6).

Table 6: Size-weight relationship for the component species of the Cachirra event

Species Relationship parameters
n Equation a b r 2
C. spixii 74 W=0,01850 L2,9730 0,01850 2,9730 0,9354
E. saurus 117 W=0,01830 L2,8669 0,01830 2,8669 0,8080
M. curema 99 W=0,00807 L2,4358 0,00807 2,4358 0,9565
M. incilis 584 W=0,03280 L2,7602 0,03280 2,7602 0,9764
M. liza 204 W=0,05460 L2,5857 0,05460 2,5857 0,8560

Source: Authors

Mugilids were the most abundant species, both before and during the Cachirra event. We identified a marked difference in CF and RI values before and after the mortality process. M. curema reached its highest CF value (2,10); and E. saurus and M. liza showed the highest RI values before the Cachirra event (1,80 and 1,70). M. liza and M. incilis had the highest values (0,58 and 0,40) after the event (Table 7).

Table 7: Number of individuals (n) by species and descriptive statistics of the variables TL, TW, CF, and RI before and after the Cachirra event

Species TL (cm) TW (g) CF RI
N Max. Avg. σ Max. Avg.
Before the Cachirra event
C. spixii 74 26,3 20,48 3,93 293 162,70 1,89 1,30
E. saurus 117 26,2 19,56 4,09 320 110,03 1,47 1,80
M. curema 99 30,0 14,68 4,50 270 66,40 2,10 1,60
M. incilis 584 39,8 19,28 5,26 736 138,05 1,92 1,50
M. liza 204 37,0 18,68 3,91 430 117,32 1,80 1,70
After the Cachirra event
C. spixii 26 20 11,61 3,143 52 12,84 0,82 0,37
E. saurus 734 35 18,80 5,418 136 41,34 0,62 0,26
M. curema 634 24 12,52 2,950 92 22,77 1,16 0,40
M. incilis 518 38 17,37 5,327 442 53,79 1,02 0,49
M. liza 211 38 19,30 7,465 438 73,47 1,02 0,58

n: number of individuals; Max: maximum; Avg: average; σ: standard deviation; CF: condition factor; RI: repletion index

Source: Authors

Table 8 shows the stomach contents of different species that constitute the Cachirra event. During the wet season, the food supply is very diverse, predominantly consisting of organic matter, crustacean remnants, detritus, among others. Conversely, the food supply is meager during the dry season.

Table 8: Stomach content of some component species of the Cachirra event

Species Type of food
Rainy season Drought season
E. saurus Detritus, fish remains crustacean remains, and shrimp. Crustacean remains
M. liza Organic matter, vegetal detritus, sediments, diatoms, copepods, algae, mud, and organic detritus. Organic detritus
M. incilis Organic matter, plant detritus, sediments, diatoms, copepods, crustaceans, algae, mud, and organic detritus. Organic matter and detritus
M. curema Organic matter, plant detritus, sediments, diatoms, copepods, mud, organic detritus, and crustacean remains. Mud and organic detritus
C. spixii Seaweed and shrimp postlarvae. Vegetal detritus
M. furnieri Organic detritus, ostracods, and bivalves. Organic detritus
C. ensiferus Fish and shrimp remains, detritus, insects, crabs, and crustacean remains. Crustacean remains

Source: Authors

Discussion

We identified different factors that interact with salinity to significantly reduce the water column during the Cachirra event in the NQL. From October to March, variables such as sunshine, evaporation, winds, and cloudiness showed a high correlation with the water temperature of the lagoon, as well as with the increase in salinity (Table 9). During these months, water temperature records showed minor variations. These changes did not affect the fish metabolism. Additionally, the water column did not exceed 30 cm in March, and the action of the northeastern winds, known by the locals as Northeast or trade winds, plays a vital role in the dynamics of the NQL. The wind's strength and origin also determine the climatological (Table 2) and oceanographic features of the area.

Table 9: Correlation matrix of climatological and physicochemical variables

Variables RT RH SU MW PR EV CL S pH DO WT NI AM
RT 1
RH 0,495 1
SU -0058 -0,851** 1
MW -0,573* -0,992** 0,797** 1
PR 0,516* 0,867** -0,757** -0,848** 1
EV -0,375 -0,914** 0,730** 0,910** -0,825** 1
CL 0,539* 0,882** -0,796** -0,898** 0,853** -0,793** 1
S -0,610* -0,707** 0,315 0,716** -0,676 0,766** -0,432 1
pH -0,354 -0,845** 0,791** 0,798** -0,726 0,629* -0,598* 0,624* 1
DO -0,102 0,265 -0,075 -0,270 0,163 -0,609* 0,074 -0,528* 0,038 1
WT 0,554* 0,802** -0,748** -0,807** 0,646* -0,503* 0,808** -0,323 -0,796** -0,329 1
NI 0,717** 0,552* -0,336 -0,546* 0,649* -0,305 0,427 -0,611* -0,753** -0,342 0,658* 1
AM -0,186 0,516* -0,624* -0,488 0,549* -0,735** 0,581* -0,223 -0,151 0,626* 0,092 -0,273 1
* The correlation is significant at a level of 0,05 (2-tailed).
** The correlation is significant at a level of 0,01 (2-tailed).
RT = Room temperature S = Salinity
RH = Relative humidity pH = Potential of Hydrogen
S = Sunshine DO = Dissolved oxygen
MW = Maximum wind WT = Water temperature
PR = Precipitation NI = Nitrites
EV = Evaporation AM =Ammonium
CL = Cloudiness

Source: Authors

Table 9 shows the different correlations that occur between the climatic and physicochemical variables. Salinity is negatively correlated with wind (r = -0,716) and relative humidity (r = -0,707), but positively with evaporation (r = 0,766). The water temperature shows positive correlations with relative humidity (r = 0,802) and cloudiness (r = 0,808), but negative ones with sunshine (r = -0,748), wind (r = -0,807), and pH (r = 0,796). In turn, the pH has a negative correlation with water temperature (r = -0,796) and nitrite (r = -0,753), but a positive one with salinity (r = 0,624).

In Figure 2, two major associations are described: the first, defined by the variables precipitation, relative humidity, cloudiness, water temperature, nitrite, ambient temperature, dissolved oxygen, and ammonia; and the second, which comprises winds, evaporation, salinity, sunshine, and pH. According to the Wilcoxon test, there are no significant differences in the average behavior of the physicochemical variables in the rainy and dry seasons (p>0,05).

Correlation horizon between climatological and physicochemical variables (October-March)

Figure 2: Correlation horizon between climatological and physicochemical variables (October-March)

Source: Authors

Our data (Table 3) showed atypically high values of NO2 - and NH4 + from October to November. During this season, the lagoon receives the most significant water contribution from the Camarones river. Most variables except salinity showed no variations that affected the existing species. In the NQL, the increments in salinity are gradual, varying from 35 ± 0,36 to 67,4 ± 1,36 PSU. Therefore, toxicity is also reduced, and, in October and September, NO2 - and NH4 + reach their maximum values while salinity reaches its minimum values. These changes, according to Partridge and Jenkins (2002), may lead to fish stress, exerting its most significant effect at 67,4 ± 1,36 PSU. Water is essential for life, and maintaining its quality is vital (Bueno et al., 2019). Values to protect aquatic animals from nitrogen compound toxicity have been proposed and recommended by different authors (EEA, 2005; Alonso, 2006; CCME, 2010). However, the recommended values are well below the data found during the wet season within the framework of this study. Neither fish nor crustacean mortality have ever been observed in this season. Therefore, we can infer that salinity is the determining factor in the mortality of these species in the NQL, as shown in Table 5.

It is emphasized that the concentration of minerals in shallow water bodies varies significantly from one brackish water body to another, due to differences in climatic, geographical, and topographic conditions, in biological activity, and in the time of analysis. The soil and the erosion or mineralization of rocks constitute edaphic sources of ions for freshwater bodies and eventually for salty bodies (Fuentes & Massol-Deyá, 2002). Bodies of water can be typified according to their total mineral content. Estuarine mineralization is affected by different climatic factors (winds, hours of illumination, precipitation, evapotranspiration, tides, solar brightness) and hydrological factors (current river discharge and tides) in such a way that, in rainy seasons, the salinity shows a tendency towards 0 UPS, as well as during low tides and in times of rising in the rivers that form the estuaries. On the other hand, in periods of drought or high tide, it tends to increase along with the minerals. Salinity depends on the stratification of the estuary. Thus, in estuaries with a saline wedge, salinity increases (Rosado & Castro-Echavez, 2011).

The inventory of species of the NQL showed that it posseses a great wealth of fish coming from the sea and, in a lesser extent, from its tributaries. Our data (Table 4) indicate that, out of the 20 families and 34 species reported, only 12 species (which represent 35,5% of the total population) are part of the Cachirra event. Our study and the one by SENA and Ministerio de Ambiente y Desarrollo Sostenible (1998) showed similar results, but notable discrepancies were observed in the number of species living in the NQL. Our study found commercially relevant species usually sold at high prices in regional and national markets, such as different types of prawns (P. schmitti and P. notialis, P. monodon), sea bass (C. undecimalis and C. ensiferus), and mugilids (M. liza, M. incilis, and M. curema). The aforementioned species are the foundation of the economy of the communities located around the NQL.

From January to March, an abrupt alteration of conditions begins, and salinity increases from 35 ± 0,36 to 67,4 ± 1,36 PSU (Table 3). This change causes a notable loss in the lagoon’s biological biodiversity because salinity (Smyth & Elliott, 2016), temperature (Molina et al., 2020), and turbidity (Romero-Berny et al., 2020) influence the spatial and temporal composition of fish communities. Furthermore, Smyth and Elliott (2016) indicate that there is also an energetic cost required in order to adapt to a changing ambient salinity, which may have consequences for organisms. Therefore, the variation from 34 species in October 2016 to 12 species in March 2017, allows stating that the salinity increase is a prominent factor that affects species mortality. The result is a decrease in the number of susceptible species, which also shows the persistence of those more abundant species, as is the case of mugilids such as M. curema, M. incilis, and M. liza. In some cases, fish can survive due to their osmoregulation capabilities (Stone et al., 2014) and their eating habits when a high concentration of nutrients are available due to evaporation in hypersaline environments, which agrees with what was indicated by Arjonilla and Blasco (2003) regarding the salinity-evaporation parameter, which increases the concentration of both ammonium and silicates.

Organisms from euryhaline environments, namely M. liza and E. saurus, can adapt to high salinities (Costa et al., 2008) during the dry season, but they do not forfeit their level of acclimatization during the wet season, which contributes to their distribution through salt adaptation (Chung, 2001). This acclimatization extends to other species such as crustaceans and tropical mollusks. Serrano et al. (2011) observed successful acclimatization of gray snapper (L. griseus) juveniles to hyposaline and hypersaline environments (0-60 PSU) after an adjustment of 96 h, thus demonstrating that ranges of acclimatization to changes in salinity vary from species to species.

In general, the studied species exhibit different values corresponding to negative allometric growth (Table 6), except C. spixii, which presented an isometric growth ,with a B value almost equal to 3,0 (2,9730). Negative allometric growth means species have little weight for their length. Cachirra event constituents, whose B value is less than 3,0, gain length in less time than it takes for their weight to increase, as is the case of E. saurus and the mugilids (M. curema, M. incilis, and M. liza). The growth of these species does not increase as a function of size cubic power; these variations depend on time and the sampling system used. Bravo et al. (2009) reported comparable results for H. aurolineatum, an abundant species in Margarita Island (Venezuela). Studies with various species and environments support the finding that it was possible to ensure that B values ranged between 2,5 and 4,0. Under natural conditions, these values are rarely equal to 3,0, a fact that coincides with the results obtained in our study.

Fishermen in the area use ​​selective fishing gear with mesh eyes ranging from – to 1, which is known as ‘shrimp chinchorro’. This equipment allows older fish to be captured and juveniles to escape. The use of shrimp chinchorros explains that the vast majority of fish sizes before and after the Cachirra event are well below the average, corresponding to juvenile fish that have not yet achieved their first maturation, a condition reflected in the high values ​​of the CF reached by the species, especially by juvenile mugilids. During December, mugilids abound in the coastal zone and penetrate the lagoon in search of refuge and food. Guerra and Marín's (2002) study of M. liza in the Unare Lagoon in Venezuela determined that this species reaches an average size of 67,3 cm, and Ruiz and Ramírez (2002) indicate an average length of 23,1 cm for M. incilis. Both sizes are above the sizes reported for these species before and after the Cachirra event, thus reinforcing the hypothesis that most of the components of this event are in juvenile stages. It is worth adding that fish length-weight relationships may vary according to sex, sexual maturity, and food consumption.

Botero-Arango and Castaño-Rivera (2005) concluded that the fact that they did not find any statistical evidence relating the environmental variables to the CF does not discard their influence on fish welfare. In contrast, Osorio (1985) concluded that CF values are higher in September, October, and November, when environmental conditions such as lagoon depth and salinity are less extreme, which agrees with the values obtained in the present study. Although there was no consistent finding of heavier fish with a higher CF before the Cachirra event, it was observed that mugilids showed high CF values, thus reflecting a better condition or nutritional status, increased by the amount of detritus brought by the rivers during the wet season, which constitutes the primary source of food for mugilids (Osorio-Dualiby, 2016).

The difference found in the RI before and after the Cachirra event (Table 7) agrees with Franco and Bashirullah's (1992) study. These authors found that specimens with empty stomachs (RI<0,5) are larger than those that with an RI> 0,5. The abundance and biodiversity of food during the wet months explains that fish before the Cachirra event have higher RI than after the event. Alcocer (1997) argues that biodiversity reduction in saline lakes can be very drastic, especially in hypersaline lakes, which may be limited to a primary producer or another biotic group with high osmoregulatory capacities, as is the case of E. saurus and M. liza.

Castro-Aguirre (1982) and Raz-Guzmán (1995) highlighted the great influence that environmental variations and biological processes exert on the structure and dynamics of estuarine communities. According to the latter, salinity and temperature are the most relevant factors. Guevara et al. (2007) found that, during the rainy season in the Términos lagoon (Mexico), penaeid shrimp (Peneidae) and crustaceans predominate in the stomach contents of fish, decreasing during the dry season, which corresponds to December, January, and February in the NQL.

Some studies demonstrate the variation in the stomach contents of the main component species of the Cachirra event (Table 8) such as the mugilids Mugil curema, M. incilis, and M. liza, which feed mainly on phytoplankton and secondarily on debris. Mugil curema exhibits the highest consumption of phytoplankton among the three species. These results are similar to those reported by Osorio-Dualiby (2016). Franco and Bashirullah (1992) reported that M. curema feeds preferentially on benthic diatoms, organic debris, inorganic fine sediments, and dinoflagellates. Gómez-Canchong et al. (2004) indicated that M. incilis has a high consumption of detritus, followed by phytoplankton and a very low consumption of zooplankton. Bustos and Pérez (2003) and Cogua et al. (2013) indicated that M. incilis preferably consumes centric diatoms and pennadas and that Mugil liza showed a high consumption of phytoplankton and a low consumption of detritus.

CONCLUSIONS

Climatological, physicochemical, and food availability variables in the dry season exert significant effects on the composition and mortality of fish species in the NQL. These variables determine a sequence of mortality due to the progressive increase in salinity known as the Cachirra event. Mugilidae is a family with a higher number of species resistant to salinity increases, which is due to its great osmotic potential and better nutritional status. Most of the components of the Cachirra event are in juvenile stages. Their length-weight relationship can vary according to sex, sexual maturity, and food intake.

The mineralization of the Navío Quebrao lagoon is affected by different climatic factors (winds, hours of illumination, precipitation, evapotranspiration, tides, solar brightness) and hydrological factors (discharge from the river, current, and tides), as well as by the winds, high temperatures, salinity increases, and accelerated clogging by transport and dumping of sediments by its tributaries, the latter being the most important and meriting the implementation of public strategies that lead to mitigating the felling of trees and extractive activities of the Camarones riverbed, considering that the Cachirra event plays an important role in the cultural identity of the inhabitants of Camarones and serves as sustenance for the economy of the indigenous communities located in their surroundings.

Acknowledgements

ACKNOWLEDGMENTS

The authors would like to thank the indigenous communities settled around the Navío Quebrao Lagoon and the residents of the Camarones village for providing invaluable information about the Cachirra event and the various ways to prepare these fish.

BIBLIOGRAPHY

Al-Khshali, M. S. (2017). Effect of Salinity on Feed Conversion Rate, Feed Conversion Efficiency, Protein Intake and Efficiency of Protein Utilization Ratio in Common Carp Cyprinus Carpio. American Journal of Life Sciences. Special Issue: Environmental Toxicology, 5(3-1), 30-35. https://www.sciencepublishinggroup.com/journal/paperinfo?journalid=118&doi=10.11648/j.ajls.s.2017050301.15 [Link]

Alcocer, J. (1997). Biodiversidad y lagos salinos. Biodiversitas, 3(16), 7-14. https://bioteca.biodiversidad.gob.mx/janium/Documentos/1405.pdf [Link]

Almeida, P. R. (2003). Feeding ecology of Liza ramada (Risso, 1810) (Pisces, Mugilidae) in a south-western estuary of Portugal. Estuarine, Coastal, and Shelf Science, 57(1-2), 313-323. https://doi.org/10.1016/s0272-7714(02)00357-8 [Link]

Alonso, A. (2006). Valoración de la degradación ambiental y efectos ecotoxicológicos sobre la comunidad de macroinvertebrados bentónicos en la cabecera del río Henares. Ecosistemas, 5(2), 101-105. https://www.revistaecosistemas.net/index.php/ecosistemas/article/view/512/488 [Link]

Annichiarico, N. & Guzmán, J. (2006). Diseño de un sistema de monitoreo e implementación de un modelo de simulación de balance hídrico y salinidad de la laguna costera Navío Quebrado, La Guajira colombiana [Undergraduate thesis, Universidad de la Guajira].

APHA, AWWA, & WEF. (2012). Standard methods for the examination of water and wastewater (22nd ed.). American Public Health Association.

Arjonilla, M., & Blasco, J. (2003). Análisis de nutrientes en aguas estuáricas. Efecto de la salinidad. Ciencias Marinas, 29(4), 389-395. https://doi.org/10.7773/cm.v29i4.177 [Link]

Bedoya, C. J. (2004). Caracterización de la pesquería artesanal en la laguna Navío Quebrado. departamento de la Guajira, Caribe Colombiano [Undergraduate thesis, Universidad Jorge Tadeo Lozano]. http://hdl.handle.net/20.500.12010/1359 [Link]

Botero-Arango, J., & Castaño-Rivera, F. (2005). Inducción de la madurez gonadal del pargo palmero lutjanus analis (pisces: lutjanidae) mediante la aplicación de un fototermoperiodo artificial de acondicionamiento. Boletin de Investigaciones Marinas y Costeras, 34, 69-79. https://doi.org/10.25268/bimc.invemar.2005.34.0.234 [Link]

Bravo, E., Eslava, N., & González, L. (2009). Crecimiento y mortalidad natural del pez Haemulon aurolineatum (Teleostei: Haemulidae) del suroeste de la isla de Margarita, Venezuela. Revista de Biologia Tropical, 57(3), 699-706. https://doi.org/10.15517/rbt.v57i3.5485 [Link]

Bueno, S. E., Marceleño, S., Nájera, O., & De Haro, R. (2019). Implementación del método de escasez en la determinación de la huella hídrica en la zona costera de San Blas, México. Revista Tecnura, 23(62), 45-54. https://doi.org/10.14483/22487638.15796 [Link]

Bustos, D., & Pérez, D. (2003). Ecología trófica y algunos aspectos biológicos de las especies pertenecientes a las familias Mugilidae y Centropomidae en la laguna de Navío Quebrado, Guajira, Caribe colombiano [Undergraduate thesis, Universidad Jorge Tadeo Lozano]. http://hdl.handle.net/20.500.12010/1344 [Link]

Camargo, J. A., & Alonso, Á. (2006). Ecological and toxicological effects of inorganic nitrogen pollution in aquatic ecosystems: A global assessment. Environment International, 32(6), 831-849. https://doi.org/10.1016/j.envint.2006.05.002 [Link]

Canadian Council of Ministers of the Environment (CCME). (2010). Canadian water quality guidelines for the protection of aquatic life: Ammonia. Canadian Environmental Quality Guidelines. https://ccme.ca/en/res/ammonia-en-canadian-water-quality-guidelines-for-the-protection-of-aquatic-life.pdf [Link]

Cardona, L. (2001). Non-competitive coexistence between Mediterranean grey mullet: evidence from seasonal changes in food availability, niche breadth and trophic overlap. Journal of Fish Biology, 59(3), 729-744. https://doi.org/10.1111/j.1095-8649.2001.tb02376.x [Link]

Castro-Aguirre, J. L. (1982). Los peces de las lagunas Oriental y Occidental, Oaxaca, México y sus relaciones con la temperatura y salinidad. II. Análisis multifactorial. Anales de La Escuela Nacional de Ciencias Biológicas, 26(1-4), 85-100. https://biblat.unam.mx/hevila/AnalesdelaEscuelaNacionaldeCienciasBiologicas/1982/vol26/no1-4/5.pdf [Link]

Cervigón, F., & Fischer, W. (1979). Infopesca. Catálogo de especies marinas de interés económico actual o potencial para América Latina. Parte I. Atlántico Centro y Suroccidental (SIC/79/1). FAO/UNDP.

Chasqui-Velasco, L., Polanco, A., Acero, A., Mejía-Falla, P., Navia, A., Zapata L. A., & Caldas, J. P. (Eds). (2017). Libro Rojo de peces marinos de Colombia. Instituto de Investigaciones Marinas y Costeras Invemar, Ministerio de Ambiente y Desarrollo Sostenible.

Chung, M. (2001). Adaptabilidad de una especie eurihalina Oreochromis mossambicus (Peters, 1852) en aguas saladas de la zona nororiental de Venezuela. Revista de Biología Tropical, 49(1). https://www.scielo.sa.cr/scielo.php?script=sci_arttext&pid=S0034-77442001000100002 [Link]

Cogua, P., Jiménez-Reyes, M. F. & Duque, G. (2013). Relaciones tróficas de cinco especies de peces de interés comercial en la bahía de Cartagena, Caribe colombiano. Boletín de Investigaciones Marinas y Costeras, 42(1), 185-192. https://doi.org/10.25268/bimc.invemar.2013.42.1.68 [Link]

Costa, L. D. F., Miranda-Filho, K. C., Severo, M. P., & Sampaio, L. A. (2008). Tolerance of juvenile pompano Trachinotus marginatus to acute ammonia and nitrite exposure at different salinity levels. Aquaculture, 285(1-4), 270-272. https://doi.org/10.1016/j.aquaculture.2008.08.017 [Link]

Crosetti, D., & Cataudella, S. (1995). Grey mullet culture. In C.E. Nash (Ed.) World Animal Science 34B: Production of Aquatic Animals (pp. 271-288). Elsevier.

de la Lanza-Espino., G. Hernández-Pulido., S., & Gutiérrez-Mendieta., F. J. (2020). Inconvenientes del uso de promedios de parámetros fisicoquímicos no conservativos, ejemplos de caso lagunas costeras mexicanas. Revista Tecnura, 24(65), 85-101. https://doi.org/10.14483/22487638.15973 [Link]

dos Santos, E. D. (1978). Dinâmica de populações aplicada à pesca e piscicultura. Editora Hucitec edusp.

European Environmental Agency (EEA) (2005). Source apportionment of nitrogen and phosphorus inputs into the aquatic. Report No 7. EEA.

Fernández-Delgado, C. Drake, P. Arias, A.M. & García-González, D. (2000). Peces de Doñana y su entorno. Organismo autónomo de parques nacionales. Editorial OAPN.

Franco, L., & Bashirullah, K. M. B. (1992). Alimentación de la lisa (Mugil curema) del Golfo de Cariaco-Estado Sucre, Venezuela. Zootecnia Tropical, 10(2), 219-238. https://baixardoc.com/preview/alimentacion-de-la-lisa-mugil-curema-del-golfo-de-cariaco-estado-suche-venezuela-5cdf1a12193ee [Link]

Froese, R. (2006). Cube law, condition factor and weight-length relationships: history, meta-analysis and recommendations. Journal of Applied Ichthyology, 22(4), 241-253. https://doi.org/10.1111/j.1439-0426.2006.00805.x [Link]

Fuentes, F., & Massol-Deyá, A. (2002). Manual de laboratorios: ecología de microorganismos. Editorial Universidad de Puerto Rico.

Gómez-Canchong, P., Manjarrés, L.M., Duarte, L. O., & Altamar, J. (2004). Atlas pesquero del área norte del mar Caribe de Colombia. Universidad del Magdalena.

Guerra, A. & Marín, G. (2002). Algunos aspectos biológicos y pesqueros del lebranche (Mugil liza) en la laguna de Unare, estado Anzoátegui, Venezuela. Zootecnia Tropical, 20(3), 287-305. http://ve.scielo.org/scielo.php?script=sci_arttext&pid=S0798-72692002000300002 [Link]

Guevara, E., Álvarez, H., Mascaró, M., Rosas, C., & Sánchez, A. (2007). Hábitos alimenticios y ecología trófica del pez Lutjanus griseus (Pisces: Lutjanidae) asociado a la vegetación sumergida en la Laguna de Términos, Campeche, México. Revista de Biología Tropical, 55(3-4), 989-1004. https://doi.org/10.15517/rbt.v55i3-4.5972 [Link]

Huxley, J. S. (1950). Relative Growth and Form Transformation. Proceedings of the Royal Society B: Biological Sciences, 137(889), 465-469. https://doi.org/10.1098/rspb.1950.0055 [Link]

Instituto de Hidrología, Meteorología y Estudios Ambientales de Colombia. (IDEAM) (2017). Reportes climáticos zona Navío Quebrao 2016-2017. IDEAM.

Molina-Ocampo, R. (1993). Hábitos alimenticios de peces pelágicos menores de importancia comercial del Golfo de California, México [Master's thesis, Instituto Tecnológico de Estudios Superiores de Monterrey].

Molina, A., Duque, G., & Cogua, P. (2020). Influences of environmental conditions in the fish assemblage structure of a tropical estuary. Marine Biodiversity, 50(1), 1-13. https://doi.org/10.1007/s12526-019-01023-0 [Link]

Nardini, A. (2005). Documentos de modelación matemática para la Laguna Navío Quebrado. Riohacha, La Guajira. Ricerca e Corporazioni.

Negri, S. (2000). Informe Final Ingeniería Hidráulica. Proyecto Prolagunas, Ricerca e Cooperazione..

Oliva-Paterna, F. J., Andreu, A., Minano, P. A., Verdiell, D., Egea, A., de Maya, J. A., Ruiz- Navarro, A., García-Alonso, J., Fernández-Delgado, C., & Torralva, M. (2006). -O-Y fish species richness in the littoral shallows of the meso-saline coastal lagoon (Mar Menor, Mediterranean coast of the Iberian Peninsula). Journal of Applied Ichthyology, 22(3), 235-237. https://doi.org/10.1111/j.1439-0426.2006.00717.x [Link]

Osorio-Dualiby, D. (1985). Ecología trófica de Mugil curema, M. incilis y M. Liza (Pisces: Mugilidae) en la Ciénaga Grande de Santa Marta. [Undergraduate thesis, Universidad Nacional de Colombia].

Osorio-Dualiby, D. (2016). Ecologia trofica de Mugil curema, M. incilis y M. liza (Pisces: Mugilidae) en la Cienaga Grande de Santa Marta, Caribe Colombiano. I. Análisis Cualitativo y Cuantitativo. Boletín de Investigaciones Marinas y Costeras, 18, 446. https://doi.org/10.25268/bimc.invemar.1988.18.0.446 [Link]

Partridge, G. J., & Jenkins, G. I. (2002). The effect of salinity on growth and survival of juvenile black bream (Acanthopagrus butcheri). Aquaculture, 210(1-4), 219-230. https://doi.org/10.1016/S0044-8486(01)00817-1 [Link]

Pauly, D. (1984). Fish populations dynamics in tropical waters: a manual for use with programmable calculators. WorldFish.

Pérez, Y. & Ceballos, J. M. (2002). Formulación y validación social de una propuesta de reglamentación en el aprovechamiento artesanal sostenible del recurso camarón (Pennaeus sp.) en el Santuario de Fauna y Flora Los Flamencos, Caribe Colombiano [Undergraduate thesis, Universidad de La Guajira].

Raz-Guzmán, A. (1995). Caracterización trófica de los componentes dominantes de las comunidades bentónicas en Laguna de Términos, Campeche y en la plataforma continental adyacente [Unpublished doctoral thesis, Universidad Autónoma de México].

Ricerca e Cooperazione - Corpoguajira. (2001). Proyecto Prolagunas. Protección y recuperación de humedales costeros del Caribe Colombiano. La Laguna de Navío Quebrado, el ambiente y su gente. Universidad Jorge Tadeo Lozano.

Román, B. (1979). Peces Marinos de Venezuela: claves dicotómicas de los géneros y las especies. Sociedad de Ciencias Naturales La Salle, 39(111-112), 5-408. http://flasa.msinfo.info/portal/bases/biblo/texto/peces_marinos_venezuela.pdf [Link]

Romero-Berny, E. I., Velázquez-Velázquez, E., Schmitter-Soto, J. J., & Salgado-Ugarte, I. H. (2020). The influence of habitat on the spatio-temporal dynamics of fish assemblages in a lagoon-estuarine system of the mexican pacific. Latin American Journal of Aquatic Research, 48(1), 23-37. https://doi.org/10.3856/vol48-issue1-fulltext-2349 [Link]

Rosado, J., & Castro-Echavez, F. L. (2011). Comportamiento de las variables fisicoquímicas en los diferentes recursos hídricos del departamento de la Guajira. Editorial Gente Nueva.

Rosado, J., Díaz, L., & Márquez, E. (2011). La Laguna y La Cachirra. Editorial Gente Nueva.

Rosado, J. & Márquez, E. (2004). Efectos climáticos y fisicoquímicos sobre la formación y mortalidad de Cachirra, Laguna Navío Quebrao, LNQ, Camarones [Conference presentation]. VI seminario internacional de Limnología, Monteria, Colombia.

Rosado, J., & Cortés, L. (2006). Aspectos florísticos y ecológicos de la Laguna Navío Quebrao, Camarones, Riohacha, La Guajira, Colombia. Ciencia e Ingeniería Aplicada, 1, 9-21.

Rosas-Luis, R., Andrade, P., Avila-Tumbaco, A., & Pincay-Espinoza, J. (2016). Manual para la identificación de peces óseos marino-costeros del Pacífico ecuatoriano basado en esqueletos axiales. Manta, Manabí, Ecuador. Editorial Mar abierto.

Ruiz, J.A. & Ramírez, J. G. (2002). Valoraciones preliminares de los principales componentes bióticos y fisicoquímicos en la Laguna Navío Quebrao (Guajira, Colombia): Informe final. Ricerca e Cooperazione - European Union - Corpoguajira.

Sánchez-Hernández, J. Servia, M. Vieira-Lanero, R. & Cobo, F. (2010). Evaluación del lavado gástrico como herramienta para el análisis de la dieta en trucha común. Limnetica, 29(2), 369-378. https://doi.org/10.23818/limn.29.30 [Link]

Schofield, P. J., Peterson, M. S., Lowe, M. R., Brown-Peterson, N. J., & Slack, W. T. (2011). Survival, growth and reproduction of non-indigenous Nile tilapia, Oreochromis niloticus (Linnaeus 1758). I. Physiological capabilities in various temperatures and salinities. Marine and Freshwater Research, 62(5), 439-449. https://doi.org/10.1071/MF10207 [Link]

SENA & Ministerio de Ambiente y Desarrollo Sostenible. (1998). Diagnóstico rural rápido, Santuario de Fauna y Flora los Flamencos, corregimiento de Camarones, Riohacha. SENA, MADS.

Serrano, X., Serafy, J., & Grosell, M. (2011). Osmoregulatory capabilities of the gray snapper, lutjanus griseus: Salinity challenges and field observations. Marine and Freshwater Behaviour and Physiology, 44(3), 185-196. https://doi.org/10.1080/10236244.2011.585745 [Link]

Shikano, T., Chiyokubo, T., & Taniguchi, N. (2001). Effect of inbreeding on salinity tolerance in the guppy (Poecilia reticulata). Aquaculture, 202(1-2), 45-55. https://doi.org/10.1016/S0044-8486(01)00568-3 [Link]

Simier, M., Blanc, L., Aliaume, C., Diouf, P.S., & Albaret, J. J. (2004). Spatial and temporal structure of fish assemblages in an “inverse estuary”, the Sine Saloum system (Senegal). Estuarine, Coastal and Shelf Science, 59(1), 69-86. https://doi.org/10.1016/j.ecss.2003.08.002 [Link]

Smyth, K., & Elliott, M. (2016). Effects of changing salinity on the ecology of the marine environment. In M. Solan & N. Whiteley (Eds.), Stressors in the Marine Environment. Physiological and ecological responses; societal implications (pp. 161-174). Oxford University Press. https://doi.org/10.1093/acprof:oso/9780198718826.003.0009 [Link]

Stone, D. A. J., Roberts, S. D., & Krishna-Lee, C. (2014). Hyper-Saline Conditions Affect Growth, Osmoregulation and Survival of Fingerling and Juvenile Yellowtail Kingfish. Seriola Lalandi. Journal of Aquaculture and Marine Biology, 1(1), 19-27. https://doi.org/10.15406/jamb.2014.01.00005 [Link]

Strydom, N. A. (2003). Occurrence of larval and early juveniles fishes in the surf zone adjacent to two intermittently open estuaries, South Africa. Environmental Biology of Fishes, 66(4), 349-359. https://doi.org/10.1023/a:1023949607821 [Link]

Rosado-Vega., J.R. Castro-Echavez., F.L. y Márquez Gulloso., E.R. (2022) Environmental, Biological, and Fishing Factors Influencing Fish Mortality and Development of the Cachirra event, Navío Quebrao Lagoon. Tecnura, 26(72), 17-41. https://doi.org/10.14483/22487638.17675
This paper is the result of the research project titled Environmental, biological, and fishing factors influencing fish mortality and development of the Cachirra event, Navío Quebrao Lagoon, which was funded by the Research Center of Universidad de La Guajira.