Description
Project conducted in 2001-2002 to evaluate fauna (birds and bumblebees) and flora composition along an urbanization gradient in Trondheim.
Enregistrements de données
Les données de cette ressource données d'échantillonnage 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 56 enregistrements.
1 tableurs de données d'extension existent également. Un enregistrement d'extension fournit des informations supplémentaires sur un enregistrement du cœur de standard (core). Le nombre d'enregistrements dans chaque tableur de données d'extension est illustré ci-dessous.
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
Le tableau ci-dessous n'affiche que les versions publiées de la ressource accessibles publiquement.
Comment citer
Les chercheurs doivent citer cette ressource comme suit:
Aagaard K H, Fremstad E, Gjershaug J O (2020): Trondheim urban biodyversity survey. v1.2. NTNU University Museum. Dataset/Samplingevent. https://gbif.vm.ntnu.no/ipt/resource?r=trondheim_urban_biodyversity_survey&v=1.2
Droits
Les chercheurs doivent respecter la déclaration de droits suivante:
L’éditeur et détenteur des droits de cette ressource est Norwegian University of Science and Technology. Ce travail est sous licence Creative Commons Attribution (CC-BY) 4.0.
Enregistrement GBIF
Cette ressource a été enregistrée sur le portail GBIF, et possède l'UUID GBIF suivante : 5cd671a0-8a45-46ea-848e-d782a529cacb. Norwegian University of Science and Technology publie cette ressource, et est enregistré dans le GBIF comme éditeur de données avec l'approbation du GBIF Norway.
Mots-clé
urbanisation urbanization; Samplingevent
Contacts
- Créateur
- Associate professor emeritus
- Créateur
- Affiliated emeritus
- Créateur
- Research Professor emeritus
- Fournisseur Des Métadonnées ●
- Personne De Contact
- PhD candidate
http://orcid.org/0000-0002-7599-712X
- Utilisateur
Couverture géographique
Within the Norwegian Trondheim Municipality administrative borders. The study area was split into five sectors to reflect variation in land cover (build-up area vs. natural vegetation), age of build-up structures, and landscape architecture. The investigators subjectively determined these sectors. Within each sector, 10 plots of 100m × 100m (50 in total) were placed semi-randomly, aiming to cover most of the within-sector variation (e.g. plots randomly covering completely build-up area in the most urban sector were complemented with typical park-like plots within the sector). The most urbanised areas of the city were not included in the gradient.
| Enveloppe géographique | Sud Ouest [63,384, 10,377], Nord Est [63,441, 10,519] |
|---|
Couverture taxonomique
All vascular plants were identified to species (a few taxa only identified to genus) and recorded on a rank-aundance scale (1-4, rare - scattered - common - dominant), breeding birds (couples or stationary males) were identified to species and counted (abundance), and bumblebees were identfied to species (presence absence). All registrations were done within 100m*100m plots
| Genus | Brassica sp., Chenopoduim sp., Heracleum sp., Hieracium sp., Larix sp., Pinus sp., Sedum sp., Sorbus sp., Syringa sp. |
|---|---|
| Species | Turdus pilaris, Passer domesticus, Pica pica, Chloris chloris, Cyanistes caeruleus, Phylloscopus collybita, Fringilla coelebs, Parus major, Corvus frugilegus, Turdus iliacus, Sturnus vulgaris, Carduelis spinus, Phylloscopus trochilus, Corvus cornix, Prunella modularis, Columba palumbus, Erithacus rubecula, Corvus monedula, Emberiza citrinella, Motacilla alba, Larus canus, Turdus merula, Turdus philomelos, Sylvia communis, Muscicapa striata, Ficedula hypoleuca, Periparus ater, Fringilla montifringilla, Anas platyrhynchos, Bombus pascuorum, Bombus hypnorum, Bombus lucorum, Bombus lapidarius, Bombus hortorum, Bombus pratorum, Bombus soroeensis, Bombus bohemicus, Bombus sylvestris, Acer platanoides, Acer pseudoplatanus, Achillea millefolium, Achillea ptarmica, Aconitum septentrionale, Actaea spicata, Aegopodium podagraria, Aesculus hippocastanum, Aethusa cynapium, Agrostis capillaris, Agrostis gigantea, Agrostis stolonifera, Alchemilla glabra, Alchemilla gracilis, Alchemilla glaucescens, Alchemilla monticola, Alchemilla murbeckiana, Alchemilla propinqua, Alchemilla subcrenata, Alchemilla subglobosa, Alchemilla wichurae, Alisma plantago-aquatica, Alliaria petiolata, Alnus incana, Alopecurus geniculatus, Alopecurus pratensis, Amelanchier spicata, Andromeda polifolia, Anemone nemorosa, Angelica sylvestris, Anthoxanthum odoratum, Anthriscus sylvestris, Anthyllis vulneraria, Aquilegia vulgaris, Arabis hirsuta, Arenaria serpyllifolia, Artemisia vulgaris, Aruncus dioicus, Asplenium trichomanes, Athyrium filix-femina, Avena pubescens, Barbarea vulgaris, Betula nana, Betula pendula, Betula pubescens, Bistorta vivipara, Blechnum spicant, Calamagrostis purpurea, Calluna vulgaris, Caltha palustris, Calystegia sepium, Campanula latifolia, Campanula rapunculoides, Campanula rotundifolia, Campanula trachelium, Capsella bursa-pastoris, Cardamine amara, Carduus crispus, Cardamine hirsuta, Cardamine pratensis, Carex canescens, Carex demissa, Carex digitata, Carex echinata, Carex lasiocarpa, Carex nigra, Carex ovalis, Carex pallescens, Carex panicea, Carex pauciflora, Carex pilulifera, Carex rostrata, Carex vaginata, Carum carvi, Centaurea montana, Cerastisum arvense, Cerastium fontanum, Cerastium glomeratum, Chamomilla suaveolens, Chenopodium album, Chrysosplenium alternifolium, Cirsium arvense, Cirsium helenioides, Cirsium palustre, Cirsium vulgare, Convallaria majalis, Cornus alba, Cornus suecica, Corylus avellana, Cotoneaster lucidus, Cotoneaster villosulus, Cotoneaster villosulus, Cystopteris fragilis, Dactylis glomerata, Dactylorhiza maculata, Deschampsia caespitosa, Deschampsia flexuosa, Descurainia sophia, Drosera rotundifolia, Dryopteris carthusiana, Dryopteris expansa, Dryopteris filix-mas, Elymus caninus, Elymus repens, Empetrum nigrum, Epilobium angustifolium, Epilobium montanum, Epilobium palustre, Epilobium watsonii, Equisetum arvense, Equisetum fluviatile, Equisetum palustre, Equisetum pratense, Equisetum sylvaticum, Eriophorum angustifolium, Eriophorum latifolium, Eriophorum vaginatum, Erophila verna, Erysimum cheiranthoides, Erysimum hieraciifolium, Euphorbia helioscopia, Euphorbia sp., Fallopia ×bohemica, Fallopia japonica, Festuca ovina, Festuca pratensis, Festuca rubra, Filaginella uliginosa, Filipendula ulmaria, Fragaria vesca, Fraxinus excelsior, Fumaria officinalis, Gagea lutea, Galeopsis bifida, Galeopsis speciosa, Galium album, Galium aparine, Galium boreale, Galium palustre, Galium verum, Gentianella campestris, Geranium robertianum, Geranium sylvaticum, Geum rivale, Geum urbanun, Glechoma hederacea, Glyceria fluitans, Gymnocarpium dryopteris, Hepatica nobilis, Heracleum sibiricum, Heracleum sphondylium, Hesperis matronalis, Hippophae rhamnoides, Hypericum maculatum, Juncus alpinoarticulatus, Juncus articulatus, Juncus bufonius, Juncus conglomeratus, Juniperus communis, Knautia arvensis, Laburnum alpinum, Lamium confertum, Lamium purpureum, Lapsana communis, Lathyrus pratensis, Leontodon autumnalis, Leucanthemum vulgare, Lilium martagon, Linaria vulgaris, Linnaea borealis, Linum catharticum, Lolium multiflorum, Lolium perenne, Lonicera caerulea, Lotus corniculatus, Lupinus polyphyllus, Luzula multiflora, Luzula pilosa, Lychnis flos-cuculi, Lycopodium annotinum, Lysimachia nummularia, Lysimachia punctata, Maianthemum bifolium, Matricaria perforata, Matteuccia struthiopteris, Matteuccia struthiopteris, Melampyrum pratense, Melampyrum sylvaticum, Melica nutans, Menyanthes trifoliata, Moehringia trinervia, Molinia caerulea, Muscari botryoides, Myosotis arvensis, Nardus stricta, Orthilia secunda, Oxalis acetosella, Papaver nudicaule, Paris quadrifolia, Persicaria lapathifolia, Persicaria maculosa, Phalaris arundinacea, Phegopteris connectilis, Phleum pratense, Picea abies, Picris hieracioides, Pimpinella saxifraga, Pinguicula vulgaris, Pinus cembra, Pinus sylvestris, Plantago major, Plantago media, Platanthera bifolia, Poa alpina, Poa annua, Poa glauca, Poa nemoralis, Poa pratensis, Poa trivialis, Polygonatum multiflorum, Polygonatum odoratum, Polygala vulgaris, Populus balsamifera, Populus tremula, Potentilla anserina, Potentilla argyrophylla, Potentilla erecta, Potentilla norvegica, Potentilla palustris, Primula elatior, Prunus avium, Prunus padus, Prunella vulgaris, Pyrola minor, Ranunculus acris, Ranunculus auricomus, Ranunculus ficaria, Ranunculus repens, Raphanus sativus, Rhinanthus minor, Ribes alpinum, Ribes nigrum, Ribes rubrum, Ribes spicatum, Ribes spicatum, Rorippa palustris, Rorippa sylvestris, Rosa caesia, Rosa dumalis, Rosa majalis, Rosa mollis, Rosa rugosa, Rubus chamaemorus, Rubus idaeus, Rubus saxatilis, Rumex acetosa, Rumex acetosella, Rumex longifolius, Sagina procumbens, Salix aurita, Salix caprea, Salix lapponum, Salix myrsinites, Salix pentandra, Salix viminalis, Sambucus racemosa, Saxifraga hypnoides, Saxifraga umbrosa, Scilla sibirica, Sedum acre, Sedum aizoon, Sedum hybridum, Senecio viscosus, Senecio vulgaris, Silene dioica, Sinapis arvensis, Solidago virgaurea, Sonchus asper, Sorbus aucuparia, Sorbus hybrida, Sorbus intermedia, Sorbaria sorbifolia, Spergula arvensis, Spiraea chamaedryfolia, Stachys sylvatica, Stellaria graminea, Stellaria nemorum, Stellaria media, Succisa pratensis, Tanacetum vulgare, Thlaspi caerulescens, Trichophorum cespitosum, Trientalis europaea, Trifolium hybridum, Trifolium pratense, Trifolium repens, Triglochin palustris, Tussilago farfara, Ulmus glabra, Urtica dioica, Vaccinium myrtillus, Vaccinium uliginosum, Vaccinium vitis-idaea, Valeriana sambucifolia, Veronica beccabunga, Veronica chamaedrys, Veronica officinalis, Veronica persica, Veronica scutellata, Veronica serpyllifolia, Viburnum opulus, Vicia cracca, Vicia sepium, Vicia sylvatica, Viola arvensis, Viola palustris, Viola riviniana, Viola tricolor |
| Subspecies | Myosotis laxa caespitosa, Polygonum aviculare aviculare, Polygonum aviculare boreale, Polygonum aviculare neglectum, Sedum telephium telephium, Vaccinium oxycoccos microcarpum, Viola canina montana |
Couverture temporelle
| Date de début / Date de fin | 2001-01-01 / 2002-12-31 |
|---|
Données sur le projet
An investigation of the biodiversity and species compositions along an urbanization gradient
| Titre | Artsmangfoldet i bylandskap |
|---|---|
| Financement | Norwegian Research Council, project number 140781/720 |
| Description du domaine d'étude / de recherche | Along a gradient of urbanization within Trondheum municipality, Norway |
| Description du design | 56 100m*100m plots surveyed for plants, birds and bumblebees |
Les personnes impliquées dans le projet:
Méthodes d'échantillonnage
During field seasons in 2001 and 2002, a trained botanist from the NTNU University Museum (E. Fremstad) registered all plant species and their rank abundances on a 1-4 scale (rare – scattered – common – dominant). Regarding the birds, every plot was surveyed by walking through the plot very morning and registering all birds seen or heard. Every plot was surveyed a minimum of 5 times through the period of 7/5-2001 to 10/6-2001. The number of breeding pairs of stationary males were counted. For the bumblebees, presence or absence of single species were noted during the surveying period.
| Etendue de l'étude | The study was carried out within the Norwegian Trondheim Municipality administrative borders, around 63.42°N, 10.38°E. The study area was split into five sectors to reflect variation in land cover (build-up area vs. natural vegetation), age of build-up structures, and landscape architecture. The investigators subjectively determined these sectors. Within each sector, 10 plots of 100m × 100m (50 in total, plus 6 in addition to cover the landscape variation) were placed semi-randomly, aiming to cover most of the within-sector variation (e.g. plots randomly covering completely build-up area in the most urban sector were complemented with typical park-like plots within the sector). The most urbanised areas of the city were not included in the gradient. |
|---|
Description des étapes de la méthode:
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Métadonnées additionnelles
| Identifiants alternatifs | 5cd671a0-8a45-46ea-848e-d782a529cacb |
|---|---|
| https://gbif.vm.ntnu.no/ipt/resource?r=trondheim_urban_biodyversity_survey |