Fisheries of western Lake Tanganyika in March 2024

Occurrence
Dernière version Publié par Lake Tanganyika Floating Health Clinic le juin 3, 2024 Lake Tanganyika Floating Health Clinic
Date de publication:
3 juin 2024
Licence:
CC-BY-NC 4.0

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Description

The fish of Lake Tanganyika documented in March 2024 along the coast of Tanganyika Province, DRC.

Enregistrements de données

Les données de cette ressource occurrence ont été publiées sous forme d'une Archive Darwin Core (Darwin Core Archive ou DwC-A), le format standard pour partager des données de biodiversité en tant qu'ensemble d'un ou plusieurs tableurs de données. Le tableur de données du cœur de standard (core) contient 62 enregistrements.

Cet IPT archive les données et sert donc de dépôt de données. Les données et métadonnées de la ressource sont disponibles pour téléchargement dans la section téléchargements. Le tableau des versions liste les autres versions de chaque ressource rendues disponibles de façon publique et permet de tracer les modifications apportées à la ressource au fil du temps.

Versions

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Comment citer

Les chercheurs doivent citer cette ressource comme suit:

Mushagalusa D, Moore F, Lehman A (2024): Fisheries of Western Lake Tanganyika. v1.0. Lake Tanganyika Floating Health Clinic/WAVE. Dataset/Occurrence.

Droits

Les chercheurs doivent respecter la déclaration de droits suivante:

L’éditeur et détenteur des droits de cette ressource est Lake Tanganyika Floating Health Clinic. Ce travail est sous licence Creative Commons Attribution Non Commercial (CC-BY-NC) 4.0.

Enregistrement GBIF

Cette ressource a été enregistrée sur le portail GBIF, et possède l'UUID GBIF suivante : c58e37c4-90dd-49c1-b101-3ab9904d4854.  Lake Tanganyika Floating Health Clinic publie cette ressource, et est enregistré dans le GBIF comme éditeur de données avec l'approbation du Participant Node Managers Committee.

Mots-clé

Occurrence; Fisheries; Lake; Tanganyika; Africa; Freshwater

Contacts

Deo Mushagalusa
  • Créateur
  • Personne De Contact
  • Researcher
Centre de Recherche en Hydrobiologie
Uvira
CD
Frans Moore
  • Fournisseur Des Métadonnées
  • Créateur
  • Personne De Contact
  • Project Manager
Lake Tanganyika Floating Health Clinic/WAVE
US
Amy Lehman
  • Chercheur Principal
  • Founder/CEO
Lake Tanganyika Floating Health Clinic/WAVE
US
Amy Lehman
  • Chercheur Principal
  • CEO/FOUNDER
Lake Tanganyika Floating Health Clinic/WAVE
US

Couverture géographique

Western Lake Tanganyika within the boundaries of the Democratic Republic of the Congo.

Enveloppe géographique Sud Ouest [-6, 29,1], Nord Est [-5, 29,55]

Couverture taxonomique

Pas de description disponible

Kingdom Animalia
Phylum Chordata
Class Actinopterygii
Order Clupeiformes, Perciformes, Cichliformes, Cyprinodontiformes, Siluriformes
Family Cichlidae, Poeciliidae, Bagridae, Latidae, Clupeidae

Couverture temporelle

Date de début / Date de fin 2024-03-07 / 2024-03-18

Données sur le projet

Key biodiversity sampling of fish populations in western Lake Tanganyika.

Titre Critical Biodiversity Surveys in the Lake Tanganyika & Ruzizi River Basins
Financement JRS Biodiversity Foundation - P.O. Box 4541, Arlington VA 22204 The Nature Conservancy - 4245 North Fairfax Drive, Suite 100, Arlington, Virgina 22203-1606
Description du domaine d'étude / de recherche Western Lake Tanganyika, within the boundaries of the Democratic Republic of the Congo.
Description du design Fish sampling was carried out from local commercial caches by fishermen using various fishing gears and techniques (e.g., gillnet, seine, liftnet and handlines) when landing in nearshore villages visited at the study area and analysed at the laboratory of Biology at the Centre for Research on Hydrobiology (DR Congo).

Les personnes impliquées dans le projet:

Amy Lehman
  • Chercheur Principal
Deo Mushagalusa
Frans Moore

Méthodes d'échantillonnage

Collections of fish samples were performed once or twice per site during the study period using complementary methods in each selected station. Individuals fish species were collected in different habitats within the selected sites from local commercial catches of fishermen using their different fishing gears: gillnets of different mesh sizes and widths, beach seines and liftnets with mixed mesh sizes, gillnets with various techniques (i.e., monofilament, dormant, encircling and deep gillnets, …) and illegal mosquito nets of smaller mesh-sizes (02-03 mm). These various gears were surveyed in each sampling day and site according to the fishing habitat (lake substratum) and lake site (inshore vs. offshore). We recorded the features of each net directly at the sampling site such as the length, width (near 1.00 m) and mesh-size (near 1.00 mm) using a measuring tape or decametre. We noted the fishing depth, the duration as well as the effort (e.g., number of nets per active fishing unit, number of fisherman and net hauls) for each gear. The presence of each gear at a site allowed assessing the rate of fishing activity and fish distribution within the sampling habitats. The type of fishery and net, the numbers of fishermen involved per trip and per fishing unit were recorded and are discussed in relation to the type of gear used. After each fishing trial, fresh weight (in kg) of each sample was measured per fishing gear and number (net hauls per trip) recorded whenever possible. For each type of fishing, fish samples with a selection of species were usually bought from fishermen, and preliminary sorted at sampling sites (as fishermen did not deliver their entire fish capture) by species and after being weighed. The fish samples (handful) were collected and killed and preserved into ethanol (75%) and then fixed in formaldehyde (10%) to slow decomposition of organs. All fish species captured were identified, weighed and counted following the fishing habitat and effort. The samples were separated into smaller bags by type of fishing-gear, site and other parameters of the fishing-effort and environment and kept in 10% formaldehyde for subsequent analysis in the laboratory

Etendue de l'étude The field area was located at the northwestern part of Lake Tanganyika along the Congolese shores near and north of Baraka City in the territory of Fizi. Due to logistic constraints and field accessibility (human activities disruption or not, fishing effort) and safety, the sampling and survey sites consisted of main villages established along the coastline in these areas. This region has a tropical humid climate characterized by an alternation of wet and dry seasons and is currently subject to physical factors at different scales. All those beach fishing sites were easily accessible from each one by boat and have fishing activities as main occupation. Whenever necessary, each main site was split up into different small sub-sites according to the type of littoral habitat of the lake, i.e., sandy, rocky, mixed, and the type of fishing practices. The critical habitat of a fish species is defined as a geographic or physical area essential to the realization of the life cycle (Lévêque 1995). However, the knowledge of local communities and advices of experienced local fishermen were considered during the fish sampling in each site. At the field of investigation, some localities of high human influences are undergoing alterations (water pollution and sedimentation, fishing with unsuitable fishing gears and techniques and deforestation) with some fish species exposed to human pressures or extinction in the future.
Contrôle qualité Quality control was implemented through the steps and process outlined for all staff at the Center for Research on Hydrobiology. In addition, there was internal quality control measures that were put in place such as routine monitoring and evaluation of project progress.

Description des étapes de la méthode:

  1. At the laboratory of Biology at the Centre de Recherche en Hydrobiologie (CRH, Uvira, DR Congo) each sample was re-sorted into species by fishing gear and habitat or fishing effort and each species identified following available books and/or keys (Fryer and Iles 1972; Axelrod et al 1977; Poll 1956, 1986; Brichard 1978, 1989; Eccles 1992; Konings 2015; Fermon et al 2007) Then, specimens were sorted by species, counted and the total, standard lengths (TL and SL) and the body height (BH) were measured (nearest 0.1 mm). These measurements and measuring techniques of fish were executed according to Barel et al. (1977), Eccles (1992), Snoeks (1994), Snoeks et al (1994), Snoeks et al (1997), Snoeks (2000) and Hanssens and Snoeks (2003). Sex was determined by exanimating the genital papillae and other external body feature such as coloration patterns (Snoeks 2000). For details in the sex, fish were dissected to determine the maturity stages of gonads following De Kimpe (1964), Micha (1973), Plisnier (1990). Each fish was then weighed (using various scales following species and individual sizes), the viscera and the gonads removed, and weighed (nearest 0.001g) and the body re-weighed to calculate the gonado-somatic index (GSI).

Métadonnées additionnelles

Identifiants alternatifs c58e37c4-90dd-49c1-b101-3ab9904d4854
https://cloud.gbif.org/africa/resource?r=ltfhcfisheriesdata052924