{"help":"Return the metadata of a dataset (package) and its resources. :param id: the id or name of the dataset :type id: string","success":true,"result":[{"id":"2fe5fdae-8484-4feb-b156-1c923e0d5432","name":"2022-uk-eez-sedimentary-organic-carbon-vulnerability-ranking-estimates-gis-layers","title":"2022 UK EEZ sedimentary organic carbon vulnerability ranking estimates GIS layers","author_email":"marinescotland@gov.scot","maintainer":"Scottish Government - Marine Directorate Data Publications","maintainer_email":"marinedirectorate@gov.scot","notes":"\u003Cp\u003EThe mapping is based of secondary data sources for bottom fishing pressure (OSPAR), sediment type and organic carbon (OC) content (Smeaton et al 2021), and sediment lability as a function of grain size (Smeaton et al 2022). A new calculation methodology has been created to estimate the potential vulnerability of OC to bottom fishing induced disturbance as a function of sediment grain size and resettling speed. This allows for the potential OC lost through lateral transportation, consumption, or remineralisation as a result of bottom fishing disturbance to be estimated. By using fuzzy set theory, the potential vulnerability of sedimentary OC is estimated and mapped for the UK EEZ. All calculations and modelling were carried out within the ESRI ArcGIS software package using the spatial overlay, raster calculator and the zonal statistics tools. Full details of the study and methodology can be found in Black et al. (2022) and relevant supporting documents.\u003C\/p\u003E\n","url":"https:\/\/data.marine.gov.scot\/dataset\/2022-uk-eez-sedimentary-organic-carbon-vulnerability-ranking-estimates-gis-layers","state":"Active","private":true,"revision_timestamp":"Wed, 07\/27\/2022 - 10:07","metadata_created":"Wed, 07\/27\/2022 - 09:44","metadata_modified":"Wed, 07\/27\/2022 - 10:07","creator_user_id":"ef1d5231-9817-4ea3-875e-aadc55addee0","type":"Dataset","resources":[{"id":"187be1b1-b34f-4d2f-bdaf-7824eb2c0036","revision_id":"","url":"https:\/\/data.marine.gov.scot\/sites\/default\/files\/\/Black_et_al_2022.zip","description":"\u003Cp\u003EOutlines Layer Package\u003Cbr \/\u003E\nDescription: Country outlines for England, Scotland, Northern Ireland, Republic of Ireland, and Wales. A UK shapefile and the UK EEZ shapefile\u003Cbr \/\u003E\nis also provided.\u003C\/p\u003E\n\u003Cp\u003EType: Polygon\u003Cbr \/\u003E\nProjected Coordinate System:    British_National_Grid\u003Cbr \/\u003E\nProjection: Transverse_Mercator\u003C\/p\u003E\n\u003Cp\u003EConstants Layer Package\u003Cbr \/\u003E\nDescription: Constants used within the carbon vulnerability ranking calculation. Data sources are as follows:\u003Cbr \/\u003E\nAverage SAR (2009 - 2017) - OSPAR (\u003Ca href=\u0022https:\/\/odims.ospar.org\/en\/maps\/map-bottom-fishing-i_-surface-subsurface_khexe\/\u0022\u003Ehttps:\/\/odims.ospar.org\/en\/maps\/map-bottom-fishing-i_-surface-subsurface...\u003C\/a\u003E)\u003Cbr \/\u003E\nOrganic Carbon (OC) Content - Smeaton et al 2021\u003Cbr \/\u003E\nSediment Type - Smeaton et al 2021\u003Cbr \/\u003E\nPotential Exposure Ratio - Calculated. See: Black et al 2022 for detail.\u003Cbr \/\u003E\nSediment Lability Ratio - Smeaton et al 2022\u003Cbr \/\u003E\nCio - Calculated. See: Black et al 2022 for detail.\u003Cbr \/\u003E\nCio Linear - Calculated. See: Black et al 2022 for detail.\u003C\/p\u003E\n\u003Cp\u003EType: Raster\u003Cbr \/\u003E\nCell Size (X, Y): 0.056,0.056\u003Cbr \/\u003E\nUnits: km^2\u003C\/p\u003E\n\u003Cp\u003ECVR Calculation Layers Layer Package\u003Cbr \/\u003E\nDescription: The layers used for the carbon vulnerability ranking calculation sorted by fishing gear type. For each gear type the\u003Cbr \/\u003E\nfishing pressure (SAR), swept volume ratio (SVR), sediment lability loss (Lai), Carbon estimated to be lost (Cout), Carbon estimated to be lost\u003Cbr \/\u003E\nfuzzified (Cout Linear), and carbon vulnerability ranking (CVR) is provided. For detail on this calculation see Black et al 2022.\u003C\/p\u003E\n\u003Cp\u003EType: Raster\u003Cbr \/\u003E\nCell Size (X, Y): 0.056,0.056\u003Cbr \/\u003E\nUnits: km^2\u003C\/p\u003E\n\u003Cp\u003ECVR by gear type\/country Layer Package\u003Cbr \/\u003E\nDescription: The carbon vulnerability ranking estimate split up into territorial water boundaries. The original jerk classifications for each class (e.g. Otter CVR: Very low, low, medium, high,\u003Cbr \/\u003E\nand very high jerk values) have been applied when classifying these country splits. This is to ensure that the spatial data classifications for each gear type are comparable with each other.\u003C\/p\u003E\n\u003Cp\u003ENOTE: OTTER TRAWLING ISLE OF MAN (IOM) HAS NO RECORDS FOR VERY LOW. BEAM TRAWLING ISLE OF MAN (IOM) HAS NO RECORDS FOR VERY LOW. BEAM TRAWLING NORTHERN IRELAND (NIRE) HAS NO RECORDS FOR VERY LOW OR LOW.\u003C\/p\u003E\n\u003Cp\u003EType: Raster\u003Cbr \/\u003E\nCell Size (X, Y): 0.056,0.056\u003Cbr \/\u003E\nUnits: km^2\u003C\/p\u003E\n","format":"zip","state":"Active","revision_timestamp":"Wed, 07\/27\/2022 - 09:52","name":"022 UK EEZ sedimentary organic carbon vulnerability ranking estimates - Map Package","mimetype":"application\/zip","size":"37.41 MB","created":"Wed, 07\/27\/2022 - 09:52","resource_group_id":"f96d4bd9-9492-4e8a-b459-d66dfec8d920","last_modified":"Date changed  Wed, 07\/27\/2022 - 09:52"}],"tags":[{"id":"fc0ab477-f6cd-4f13-abc3-426e15977178","vocabulary_id":"2","name":"Carbon concentrations in sediment"},{"id":"c0c074e2-ff1c-4a12-bcf3-d30245c7b6f6","vocabulary_id":"2","name":"fishing effort"},{"id":"0c547184-a099-4b76-8405-3f8d7311a0fc","vocabulary_id":"2","name":"sediment resuspension"}],"groups":[{"description":"\u003Cp\u003EMarine Directorate undertakes a wide range of monitoring covering many aspects of the Scottish marine ecosystem.\u003C\/p\u003E\n\u003Cp\u003EMonitoring is undertaken in Scottish Inshore Waters, using networks of volunteers and automatic recording equipment, as well as in Scottish Offshore Waters, using the MSS research vessels MRV Alba na Mara and MRV Scotia.\u003C\/p\u003E\n\u003Cp\u003EMarine Scotland Science also participates national monitoring programmes, such as:\u003C\/p\u003E\n\u003Cul\u003E\n\u003Cli\u003EUK Marine Monitoring and Assessment Strategy (UKMMAS)\u003C\/li\u003E\n\u003Cli\u003EUK Marine Environmental Change Network (MECN)\u003C\/li\u003E\n\u003Cli\u003EUK Marine Environmental Data and Information Network (MEDIN)\u003C\/li\u003E\n\u003C\/ul\u003E\n\u003Cp\u003EThis group provides published data from monitoring these activities. For many activities, there are national or international standards for how the monitoring is undertaken.\u003C\/p\u003E\n","id":"f96d4bd9-9492-4e8a-b459-d66dfec8d920","image_display_url":"https:\/\/data.marine.gov.scot\/sites\/default\/files\/\/button%20220%20_1-02_1.png","title":"Monitoring","name":"group\/monitoring"},{"description":"\u003Cp\u003EMarine Directorate manages quota for fish stocks and all inshore fisheries within the 12 nautical mile territorial water limit. It is also responsible for controlling the activities of fishing vessels and fishing effort (days spent at sea) in the North Sea, west of Scotland and Faroese waters.\u003Cbr \/\u003E\nIn this section, citable data and reports relevant to fishing activities will be added.\u003C\/p\u003E\n","id":"101d17a8-ed4c-47dc-baec-0d48b9c425e5","image_display_url":"https:\/\/data.marine.gov.scot\/sites\/default\/files\/\/fisheries_white.png","title":"Fisheries","name":"group\/fisheries"}]}]}