Description
On October 25, 1994, the Portuguese Republic Vessel "S. Miguel", which was carrying a large amount of old military equipment, sank in the waters of the Portuguese continental EEZ, parallel to Lisbon. This sinking, which was attempted under controlled conditions under the Oslo Convention for the Prevention of Marine Pollution, was marred by an accident and the ship broke the sea surface before sinking. After this accident, an assessment was made of the environmental impact of the explosion and sinking of the ship. The objective was to verify a possible decrease in zooplankton biomass values in the surface layer of the water column (200 m) in the sinking area. The parameters that were considered capable of giving indications about the state of zooplankton populations were the abundance (biovolume) and the specific zooplankton diversity of the epi- (living in the 0 to 150 meters depth) and mesoplankton (living in the 150-meter depth) regions. 1000 meters deep).
Data Records
The data in this sampling event resource has been published as a Darwin Core Archive (DwC-A), which is a standardized format for sharing biodiversity data as a set of one or more data tables. The core data table contains 36 records.
2 extension data tables also exist. An extension record supplies extra information about a core record. The number of records in each extension data table is illustrated below.
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.
Versions
The table below shows only published versions of the resource that are publicly accessible.
How to cite
Researchers should cite this work as follows:
Cunha M E, Quintela F, Dos Santos A, Niza H (2021). Assessment of zooplankton at the site of the sinking of the N.R.P. "S. Miguel". Version 1.7. IPMA - Instituto Português do Mar e da Atmosfera. Samplingevent dataset. http://ipt.gbif.pt/ipt/resource?r=nrp_s_miguel&v=1.7
Rights
Researchers should respect the following rights statement:
The publisher and rights holder of this work is IPMA - Instituto Português do Mar e da Atmosfera. This work is licensed under a Creative Commons Attribution Non Commercial (CC-BY-NC 4.0) License.
GBIF Registration
This resource has been registered with GBIF, and assigned the following GBIF UUID: 381aceaa-560b-4918-989d-621706bea523. IPMA - Instituto Português do Mar e da Atmosfera publishes this resource, and is itself registered in GBIF as a data publisher endorsed by GBIF Portugal.
Keywords
Samplingevent; Zooplankton
Contacts
- Metadata Provider ●
- Originator
- Originator
- Metadata Provider ●
- Point Of Contact
- Editor ●
- Point Of Contact
Geographic Coverage
Portuguese continental EEZ, near the EEZ's outer edge and the Lisbon parallel
Bounding Coordinates | South West [36.767, -13.783], North East [38.767, -9.533] |
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Taxonomic Coverage
Zooplankton
Phylum | Ctenophora |
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Superclass | Cirripedia |
Class | Bivalvia, Gastropoda, Ophiuroidea |
Order | Calanoida, Euphausiacea, Siphonostomatoida |
Suborder | Gymnosomata |
Family | Euphausiidae, Periphyllidae, Polybiidae, Scolecitrichidae, Spionidae |
Subfamily | Prayinae |
Genus | Candacia, Centropages, Chirundina, Clausocalanus, Conchoecia, Eucalanus, Euchaeta, Euphausia, Fritillaria, Gaetanus, Nematobrachion, Nematoscelis, Oikopleura, Oithona, Oncaea, Pilumnus, Plesionika, Pleurobrachia, Pontella, Rhincalanus, Sagitta, Scaphocalanus, Stylocheiron, Thysanopoda |
Species | Acanthephyra purpurea, Acartia (Acartia) danae, Acartia (Acartia) negligens, Acartia (Acartiura) clausi, Aegisthus mucronatus, Aetideus armatus, Aetideus giesbrechti, Agalma elegans, Agetus flaccus, Bassia bassensis, Beroe ovata, Calanus helgolandicus, Candacia armata, Candacia bipinnata, Candacia ethiopica, Candacia longimana, Candacia simplex, Cavolinia inflexa, Centropages chierchiae, Ceratocymba sagittata, Chelophyes appendiculata, Chiridius poppei, Chirundina streetsii, Clausocalanus furcatus, Clausocalanus jobei, Clausocalanus lividus, Colobonema sericeum, Conchoecissa imbricata, Corycaeus clausi, Ctenocalanus vanus, Decipisagitta decipiens, Diacria trispinosa, Diogenes pugilator, Enneagonum hyalinum, Euaugaptilus magnus, Euchaeta acuta, Euchaeta media, Eucopia grimaldii, Euphausia brevis, Euphausia hemigibba, Euphausia krohnii, Euphausia similis, Evadne nordmanni, Evadne spinifera, Gaetanus minor, Gaetanus pileatus, Gennadas elegans, Gennadas valens, Goneplax rhomboides, Haloptilus longicornis, Haloptilus plumosus, Helicocranchia pfefferi, Heliconoides inflatus, Helicosalpa virgula, Heterorhabdus papilliger, Hyperia galba, Krohnitta subtilis, Lensia multicristata, Lensia subtilis, Limacina lesueurii, Lophothrix latipes, Lucicutia longicornis, Meganyctiphanes norvegica, Mesocalanus tenuicornis, Metridia brevicauda, Metridia princeps, Metridia venusta, Muggiaea atlantica, Nannocalanus gracilis, Nannocalanus minor, Nematobrachion boopis, Nematoscelis atlantica, Nematoscelis megalops, Nematoscelis microps, Neocalanus gracilis, Neognathophausia ingens, Nullosetigera helgae, Octopus vulgaris, Oithona plumifera, Oncaea venusta, Onychocorycaeus ovalis, Oplophorus spinosus, Paraeuchaeta gracilis, Paraeuchaeta hansenii, Paraeuchaeta hebes, Paraeuchaeta tonsa, Parasergestes vigilax, Pareucalanus attenuatus, Penilia avirostris, Periphylla periphylla, Phronima atlantica, Phronima colletti, Phronima sedentaria, Phronimella elongata, Phrosina semilunata, Phyllopus impar, Plesionika richardi, Pleuromamma xiphias, Processa canaliculata, Pseudevadne tergestina, Pseudoamallothrix ovata, Pseudosagitta lyra, Pterosagitta draco, Rhincalanus nasutus, Robustosergia robusta, Sagitta bipunctata, Salpa fusiformis, Salpa maxima, Sapphirina angusta, Scaphocalanus echinatus, Scina borealis, Scolecithricella dentata, Scolecithricella vittata, Scolecithrix bradyi, Scolecithrix danae, Scottocalanus persecans, Scyllarus arctus, Sergestes hanseni, Serratosagitta serratodentata, Serratosagitta tasmanica, Solenocera membranacea, Styliola subula, Stylocheiron abbreviatum, Stylocheiron longicorne, Stylocheiron maximum, Subeucalanus crassus, Subeucalanus monachus, Systellaspis debilis, Systellaspis pellucida, Temora longicornis, Temora stylifera, Thalia democratica, Themisto compressa, Themisto gaudichaudii, Thysanopoda microphthalma, Undeuchaeta major, Undeuchaeta plumosa, Urocorycaeus furcifer, Vibilia armata, Vogtia glabra |
Temporal Coverage
Start Date | 1994-11-28 |
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Start Date / End Date | 1994-12-14 / 1994-12-18 |
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Project Data
No Description available
Title | Relatório da Primeira Campanha de Monitorização do Estado das Populações de Zooplâncton apôs o Afundamento do N.R.P. "S. Miguel" |
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The personnel involved in the project:
- Author
- Author
Sampling Methods
The epizooplanktonic material was sampled in oblique trawls up to a depth of 200 m using a Bongo 60 net (circular double-mouth net 60 cm in diameter and fitted with two mesh bags of 335 and 505 m aperture). The volume of water sampled in each haul was calculated using the readings of flowmeters attached to each net's mouth. Mesozooplankton was collected using a 10 m2 mouth area Isaacs-Kidd Midwater Raul (IKMT) net with a 505 m mesh bag. The hauls took around 30 minutes to complete at the desired depth.
Study Extent | The epizooplankton was collected in 12 sampling stations, which were distributed as follows: Three stations along the Portuguese coast, one at the sinking site, four surrounding the sinking site and ten miles apart, two at the Josephine bank and one at the Bank Gorringe. |
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Method step description:
- All zooplanktonic material collected was kept in 4 percent neutral formalin, with the exception of a tiny portion of the material collected with IKMT that was frozen for examination of the concentration of heavy metals and PCBs. The biovolume of plankton samples was computed in the lab using the volume of water displaced by the organic material after large organisms (> 1 cm in epizooplankton and > 2.5 cm in mesozooplankton) were removed, and its abundance was calculated per 100 m3 of filtered water. Using a magnifying glass and a binocular microscope, species identification and enumeration were carried out in a counting chamber.
Additional Metadata
Alternative Identifiers | 381aceaa-560b-4918-989d-621706bea523 |
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http://ipt.gbif.pt/ipt/resource?r=nrp_s_miguel |