COI Metabarcoding Genetic Observations of Marine Species in the Port of Wallhamn, Sweden (2022)

Ocorrência
Versão mais recente published by University of Gothenburg on nov. 28, 2023 University of Gothenburg
Publication date:
28 de novembro de 2023
Published by:
University of Gothenburg
Licença:
CC-BY 4.0

Baixe a última versão do recurso de dados, como um Darwin Core Archive (DwC-A) ou recurso de metadados, como EML ou RTF:

Dados como um arquivo DwC-A download 662 registros em English (83 KB) - Frequência de atualização: desconhecido
Metadados como um arquivo EML download em English (29 KB)
Metadados como um arquivo RTF download em English (15 KB)

Descrição

This dataset contains genetic observations of marine species in the port of Wallhamn between June and September 2022. The observations were made using water and plankton samples, as well as samples from Autonomous Reef Monitoring Structures (ARMS) units. Species were identified using COI metabarcoding. The dataset includes ASVs (amplicon sequence variants) and their associated metadata. This dataset was published via the SBDI ASV portal (https://asv-portal.biodiversitydata.se/).

Registros de Dados

Os dados deste recurso de ocorrência foram publicados como um Darwin Core Archive (DwC-A), que é o formato padronizado para compartilhamento de dados de biodiversidade como um conjunto de uma ou mais tabelas de dados. A tabela de dados do núcleo contém 662 registros.

Também existem 1 tabelas de dados de extensão. Um registro de extensão fornece informações adicionais sobre um registro do núcleo. O número de registros em cada tabela de dados de extensão é ilustrado abaixo.

Occurrence (core)
662
dnaDerivedData 
662

This IPT archives the data and thus serves as the data repository. The data and resource metadata are available for download in the downloads section. The versions table lists other versions of the resource that have been made publicly available and allows tracking changes made to the resource over time.

Versões

A tabela abaixo mostra apenas versões de recursos que são publicamente acessíveis.

Como citar

Pesquisadores deveriam citar esta obra da seguinte maneira:

Obst M (2023). COI Metabarcoding Genetic Observations of Marine Species in the Port of Wallhamn, Sweden (2022). Version 1.4. University of Gothenburg. Occurrence dataset. https://www.gbif.se/ipt/resource?r=gu-2022-wallhamn-coi&v=1.4

Direitos

Pesquisadores devem respeitar a seguinte declaração de direitos:

O editor e o detentor dos direitos deste trabalho é University of Gothenburg. This work is licensed under a Creative Commons Attribution (CC-BY 4.0) License.

GBIF Registration

Este recurso foi registrado no GBIF e atribuído ao seguinte GBIF UUID: 37115f2e-a550-40c7-bc2c-f6b697fa7aca.  University of Gothenburg publica este recurso, e está registrado no GBIF como um publicador de dados aprovado por GBIF Sweden.

Palavras-chave

Occurrence; Observation

Contatos

Matthias Obst
  • Provedor Dos Metadados
  • Originador
  • Ponto De Contato
Project Leader
Gothenburg University
SE

Cobertura Geográfica

This dataset covers the port of Wallhamn (Sweden) which has both a commercial/industrial part in the North and a marina in the South.

Coordenadas delimitadoras Sul Oeste [58,004, 11,697], Norte Leste [58,011, 11,703]

Cobertura Taxonômica

N/A

Reino Chromista, Animalia, Unassigned
Filo Mollusca, Arthropoda, Annelida, Chordata, Myzozoa, Phoronida, Cnidaria
Class Hydrozoa, Dinophyceae, Polychaeta, Phoronida_X, Insecta, Bivalvia, Copepoda, Mammalia, Gastropoda
Ordem Diptera, Calanoida, Ostreida, Gonyaulacales, Polychaeta_X, Cephalaspidea, Phyllodocida, Gastropoda_X, Venerida, Littorinimorpha, Carnivora, Phoronida_XX, Cyclopoida, Leptothecata
Família Pectinariidae, Campanulariidae, Canidae, Gonyaulacales_X, Veneridae, Cerithiidae, Phoronidae, Oithonidae, Chironomidae, Philinidae, Spionidae, Ostreidae, Hydrobiidae, Nereididae, Centropagidae, Acartiidae

Cobertura Temporal

Data Inicial / Data final 2022-06-23 / 2022-09-09

Dados Sobre o Projeto

A comparison between eRAS (extended rapid assessment) and DNA-based identification of native and invasive species has been performed based on sampling in the port of Wallhamn. Wallhamn has been chosen out of five harbours (Strömstad, Smögen, Kungshamn, Oxelösund, Wallhamn) based on its proximity to Gothenburg and the fact that it is an established harbour with a large number of ships calling every year.

Título Övervakning främmande arter: jämförelse eRAS och DNA-baserad inventering Wallhamn (Tjörn)
Financiamento This project was funded by the Swedish Agency for Marine and Water Management
Descrição da Área de Estudo The port of Wallhamn (Sweden), located in a bay, has both a commercial/industrial part in the North and a marina in the South that are separated by a few hundred meters.
Descrição do Design eRAS includes growth plates, artificial habitats, scraping on existing structures, and visual observations of non-native species. The DNA-based identification is based on settling panels (ARMS), plankton samples, and eDNA from filtered water samples. The outputs of both methods were then compared to estimate their abilities to identify species and detect potential invasive species.

Métodos de Amostragem

Artificial habitats are plastic trays filled with pottery shards, a weight at the bottom to hold the trays down and a net above to keep the shards in place. On two sides, larger holes were cut to allow fish to move freely in and out of the habitat Plankton samples were taken as vertical hauls from the bottom (5-10 m) up to the surface with a 90 µm plankton bucket. The samples were fixed in 95% ethanol directly in place with an amount of alcohol that was judged to result in a sample with at least 70% ethanol. Upon return to the lab, the plankton samples were decanted and new alcohol was added to ensure that the ethanol content was sufficiently high. The samples were then stored in a freezer (-20°C) until extraction. Water samples for eDNA were taken with Ruttner retrievers at slightly different depths on the premises and pooled in a 1 litre vessel. Water was filtered on site and fixed with 95% ethanol.The filters were stored in a freezer (-20°C) until extraction.

Área de Estudo The different sampling methods had different timings over the summer 2022: The eRAS panels were put out on the 23rd of June and taken back on the 9th of September, one was in the industrial port, three were in the marina. The artificial habitats were put out on the 23rd of June and taken back on the 4th of August, one in each area. The ARMS were put out on the 23rd of June and taken back on the 9th of September, one in the industrial port and two in the marina. In the marina, three plankton samplings occurred on the 23rd of June, the 4th of August and the 9th of September (9 plankton samples in total). Similarly, in the marina, three eDNA samplings occurred on the 23rd of June, the 4th of August and the 9th of September (9 eDNA samples in total). Three scraping/RAS samplings occured on the 9th of September in the marina.
Controle de Qualidade Negative controls (blank samples) were created by the same extraction procedure but without the sampled material. No DNA could be detected in these samples, with neither Nanodrop nor Qubit. The blank samples were included in the preparation of libraries (below) as a further control for contamination during the extraction of DNA. Another negative control was performed during PCR.

Descrição dos passos do método:

  1. DNA was extracted from the filters with the Nucleospin eDNA water kit (Macherey-Nagel) using the Nagel) using the technique and standard developed in the laboratory. Concentration of DNA in the extracts was measured with the Qubit® fluorometer. Note that this measures concentration of all DNA in the sample and not specific DNA from the target species. This is done to ensure that the extractions have worked.
  2. The genetic analysis and comparison was based on two molecular markers (COI and 18S). These markers were amplified for each sample. Same PCR protocols were used for metabarcoding of the ARMS, eDNA and plankton samples The DNA libraries were sequenced with Illumina MiSeq, 2 x 300 bp.
  3. The analysis was performed in the R-environment with a DADA2 package. After initial quality control, the sequences were filtered for low quality, as well as adapters and primers were removed. Sequencing errors were corrected by calculating an error model; and after that singletons and chimeras were removed using the “pseudo-pooling” function in DADA2.
  4. The filtered and quality-controlled COI sequences were matched against the BOLD database with the python package BOLDigger. The 18S sequences were matched against the PR2 database. All subsequent analysis was performed with customized R scripts where identified species were matched against different NIS and IAS species reference lists.

Metadados Adicionais

Identificadores alternativos 37115f2e-a550-40c7-bc2c-f6b697fa7aca
https://www.gbif.se/ipt/resource?r=gu-2022-wallhamn-coi