Point data identifying the location of finfish or shellfish farms around Scotland from the Fish Health Inspectorate Aquadat database. This includes fishery sites which are ponds or other installation where farmed fish are stocked for recreational fishing (either private or commercial). The data includes the three categories: Active: is the status of a site that is stocked or fallow with the intention of restocking in the foreseeable future. Inactive: is the status of a site that is unlikely to be stocked in the foreseeable future. Deregistered: is the status applied to a site that is no longer used for the purpose of fish or shellfish production; the lease has been surrendered.
Onshore oil and gas licensing powers were devolved to Scottish Ministers on 9 February 2018. Onshore includes the marine area within territorial baselines. These datasets show onshore hydrocarbon fields, wells, and licensed blocks.
Areas of search (AoS) have been created using a multi-criteria analysis generated constraint map that shows a range of suitability for offshore wind energy locations. This constraint map is the product of overlaying and weighting 20 relevant layers in a GIS. From the least constrained/most suitable areas some broad zones are drawn. These broad areas are then refined into the AoS by investigating the geographic proximity to important offshore activities and issues. The activities considered to refine the footprint of the broad areas were: fishing, shipping, marine nature protected areas and oil and gas installations. These AoS will serve as guidance to developers and planners as to the most suitable sites for further offshore wind developments in Scottish waters. These sites provide a zone where developments will enjoy minimised obstacles to consenting and licensing whilst still benefitting from adequate resource and appropriate environmental conditions. These sites are recommended by Marine Scotland as places where the consenting and licensing process will be streamlined, expedient and efficient as the likely interactions to be encountered by developers have already been considered. Marine Scotland does not oblige developers to occupy these locations but to consider them as the most appropriate sites.
Seal haul-out sites are designated under section 117 of Marine (Scotland) Act 2010. Harassing a seal (intentionally or recklessly) at a haul-out site is an offence. “Haul-out site” means any place which the Scottish Ministers, after consulting the Natural Environment Research Council, by order designate as such for the purposes of this section.
Salmon Rivers in Scotland (2008) digital data produced by Scottish Government Marine Scotland Science with information from Fisheries Trusts and other sources.
Fisheries which returned coastal fixed engine or net and coble catches of salmon or sea trout to Marine Scotland Science from 2011 onwards. Fishery locations are repeated for each year that the fishery was active, i.e. reported catch data. More information on the Scottish Government salmon and sea trout fishery statistics is provided at http://www.gov.scot/Topics/marine/Publications/stats/SalmonSeaTroutCatches
Grey seals (Halichoerus grypus) are present around the coast of Scotland in internationally import numbers. They breed on wave-exposed rocky coasts, sometimes on sand or shingle beaches at the foot of cliffs, often on relatively remote islands, with large groups of pregnant females returning to traditional breeding sites in the autumn. This data shows the breeding colonies currently listed with the Sea Mammal Research Unit (SMRU).
Salmon Fishery Statistical Region boundaries, used by Scottish Government Marine Scotland for reporting annual statistics obtained from salmon catch returns made by the owners/occupiers/agents of salmon fisheries.(Salmon Fishery Statistical Districts amalgamated into Regions)
The annual Scottish Sea Fisheries Statistics report is aggregated into districts, which reflect the area of responsibility of the local fishery office. This dataset shows the approximate extent of each district using the 1:50,000 scale OS Meridian 2 mean high water spring coastline. The districts are for illustrative purposes only.\\n\\nThe districts were updated in the 2013 report to reflect changes in responsibility of the Ullapool fishery office and renamed the Pittenweem district as Anstruther.
These layers are the outputs of research which developed a national river temperature model for Scotland capable of predicting both daily maximum river temperature and sensitivity to climate change. The layers show the following: summer_max_tw_2015_16 – Predictions of maximum daily river temperatures for the hottest day between July 2015 and June 2016. summer_max_tw_2003 – Predictions of maximum daily river temperatures for the hottest year in the last 20 years (2003). summer_climate_change_sensitivity – Predictions of the change in river temperature that would result from a 1°C increase in air temperature. A fourth layer has been developed to combine the outputs from “summer_max_tw_2003” and “summer_climate_change_sensitivity” into a single layer that can be used to prioritise management where the relative importance of maximum temperature and temperature change are considered to be equal. This was achieved by (1) dividing the predictions of ‘summer_max_tw_2003’ and ‘summer_climate_change_sensitivity’ into 5 equal categories between the minimum and maximum observed values (2) assigning these categories a value ranging from 1 (the hottest / most sensitive rivers) to 5 (the coolest / least sensitive rivers) (3) sum the rankings (-1) to produce an overall priority ranking (1:9) where rivers ranked as 1 are the highest priority for management (i.e. high river temperature and high climate sensitivity) and 9 the lowest. Management_Priority_Layer – Management priority on a scale of 1:9 where 1 is the highest priority (i.e. high river temperature and high climate sensitivity) and 9 the lowest