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Increasing river temperatures are a threat to many of Scotland's freshwater species which are often adapted to live in cool environments. This includes ecologically and economically important freshwater fish species such as Atlantic salmon and brown trout. Management of riparian woodland is proven to protect cold water habitats. However, Scotland has ca. 108,000 km of rivers, of which only ca. 35% are protected by any substantial tree cover. Furthermore, the creation of new riparian woodland can be costly and logistically challenging compared to other forms of large scale woodland creation. It is therefore important that riparian tree planting is prioritised to areas where it can have greatest benefits for river temperature, specifically, where rivers are (1) hottest (2) most sensitive to climate change (see SRTMN Predictions: http://marine.gov.scot/information/scotland-river-temperature-monitoring-network-srtmn-predictions-river-temperature-and) and (3) can be effectively cooled by riparian woodland (see tree planting prioritisation layer). These three individual criteria can be combined with an equal weight to provide a single riparian woodland prioritisation score that looks to maximise the benefits of riparian tree planting for protecting Scotland’s rivers from the adverse effects of climate change. Details of the modelling work that produced the river temperature and climate sensitivity predictions can be found in the peer reviewed manuscript: Jackson et al (2018) ‘A spatio-temporal statistical model of maximum daily river temperatures to inform the management of Scotland's Atlantic salmon rivers under climate change.’ Details of the modelling work that identifies where riparian trees can have the greatest effect in reducing summer maximum river temperatures can be found in: Jackson, F.L., Hannah, D.M., Ouellet, V. and Malcolm, I.A. (2021) A deterministic river temperature model to prioritise management of riparian woodlands to reduce summer maximum river temperatures. Given the variety of potential tree planting options (southerly banks, northerly banks, both banks) and the need to scale results both nationally and locally, the outputs are illustrated as six layers on Marine Scotland Maps NMPi: 1. Nationally scaled tree planting prioritisation score where trees are planted on both banks 2. Nationally scaled tree planting prioritisation score where trees are planted on only the most southerly bank 3. Nationally scaled tree planting prioritisation score where trees are planted on only the most northerly bank 4. Locally scaled tree planting prioritisation score where trees are planted on both banks 5. Locally scaled tree planting prioritisation score where trees are planted on only the southerly bank 6. Locally scaled tree planting prioritisation score where trees are planted on only the northerly bank Riparian woodland prioritisation scores are on a scale of 1- 20, where 1 is low priority (low temperature, weak sensitivity to climate change and only a small reduction in temperature gained from planting trees) and 20 is high priority (high temperature, strong sensitivity to climate and a large expected reduction in temperature where trees are planted). To visualise the three bank scenarios it is necessary to produce a total of 3 spatial layers (i.e. planting both banks, planting on southerly bank, planting on northerly bank). However, the scores are consistent between these layers. To support decision making at different spatial scales layers were produced to identify priorities at a national scale and then re-scaled at a hydrometric area (regional) scale to highlight local priority areas Very small rivers (First (Strahler) order rivers on the CEH digital river network) were removed from this dataset. NAs exist where we are unable to make predictions of maximum temperature, climate sensitivity or planting potential. This includes locations in lochs or in circumstances where we cannot generate the required predictor variables.
Scottish Government (Marine Scotland)
public access limited according to Article 13(1)(e) of the INSPIRE Directive
Other details | ||
Internal code | Internally assigned metadata identifier | 6072 |
Title | The title is used to provide a brief and precise description of the dataset such as 'Date', 'Originating organisation/programme', 'Location' and 'Type of survey'. All acronyms and abbreviations should be reproduced in full. | Scotland River Temperature Monitoring Network (SRTMN) - Riparian Woodland Prioritisation Scores |
File Identifier | The File Identifier is a code, preferably a GUID, that is globally unique and remains with the same metadata record even if the record is edited or transferred between portals or tools. | Marine_Scotland_FishDAC_12347 |
Resource Identifier | This is the code assigned by the data owner. | Marine_Scotland_FishDAC_12347 |
Resource type | The resource type will likely be a dataset but could also be a series (collection of datasets with a common specification) or a service. | dataset |
Start date | This describes the date the resource starts. This may only be the year if month and day are not known | 2020-10-27 |
End date | This describes the date the resource ends. This may only be the year if month and day are not known | 2020-10-27 |
Spatial resolution | This describes the spatial resolution of the dataset or the spatial limitations of the service. | 50.00 |
Spatial resolution unit | This describes the unit of spatial resolution which for distance must be metres. | http://standards.iso.org/ittf/PubliclyAvailableStandards/ISO_19139_Schemas/resources/uom/gmxUom.xml#m |
Frequency of updates | This describes the frequency with which the resource is modified or updated i.e. a monitoring programme that samples once per year has a frequency that is described as 'annually'. | Not Planned |
Abstract | The abstract provides a clear and brief statement of the content of the resource. | Increasing river temperatures are a threat to many of Scotland's freshwater species which are often adapted to live in cool environments. This includes ecologically and economically important freshwater fish species such as Atlantic salmon and brown trout. Management of riparian woodland is proven to protect cold water habitats. However, Scotland has ca. 108,000 km of rivers, of which only ca. 35% are protected by any substantial tree cover. Furthermore, the creation of new riparian woodland can be costly and logistically challenging compared to other forms of large scale woodland creation. It is therefore important that riparian tree planting is prioritised to areas where it can have greatest benefits for river temperature, specifically, where rivers are (1) hottest (2) most sensitive to climate change (see SRTMN Predictions: http://marine.gov.scot/information/scotland-river-temperature-monitoring-network-srtmn-predictions-river-temperature-and) and (3) can be effectively cooled by riparian woodland (see tree planting prioritisation layer). These three individual criteria can be combined with an equal weight to provide a single riparian woodland prioritisation score that looks to maximise the benefits of riparian tree planting for protecting Scotland’s rivers from the adverse effects of climate change. Details of the modelling work that produced the river temperature and climate sensitivity predictions can be found in the peer reviewed manuscript: Jackson et al (2018) ‘A spatio-temporal statistical model of maximum daily river temperatures to inform the management of Scotland's Atlantic salmon rivers under climate change.’ Details of the modelling work that identifies where riparian trees can have the greatest effect in reducing summer maximum river temperatures can be found in: Jackson, F.L., Hannah, D.M., Ouellet, V. and Malcolm, I.A. (2021) A deterministic river temperature model to prioritise management of riparian woodlands to reduce summer maximum river temperatures. Given the variety of potential tree planting options (southerly banks, northerly banks, both banks) and the need to scale results both nationally and locally, the outputs are illustrated as six layers on Marine Scotland Maps NMPi: 1. Nationally scaled tree planting prioritisation score where trees are planted on both banks 2. Nationally scaled tree planting prioritisation score where trees are planted on only the most southerly bank 3. Nationally scaled tree planting prioritisation score where trees are planted on only the most northerly bank 4. Locally scaled tree planting prioritisation score where trees are planted on both banks 5. Locally scaled tree planting prioritisation score where trees are planted on only the southerly bank 6. Locally scaled tree planting prioritisation score where trees are planted on only the northerly bank Riparian woodland prioritisation scores are on a scale of 1- 20, where 1 is low priority (low temperature, weak sensitivity to climate change and only a small reduction in temperature gained from planting trees) and 20 is high priority (high temperature, strong sensitivity to climate and a large expected reduction in temperature where trees are planted). To visualise the three bank scenarios it is necessary to produce a total of 3 spatial layers (i.e. planting both banks, planting on southerly bank, planting on northerly bank). However, the scores are consistent between these layers. To support decision making at different spatial scales layers were produced to identify priorities at a national scale and then re-scaled at a hydrometric area (regional) scale to highlight local priority areas Very small rivers (First (Strahler) order rivers on the CEH digital river network) were removed from this dataset. NAs exist where we are unable to make predictions of maximum temperature, climate sensitivity or planting potential. This includes locations in lochs or in circumstances where we cannot generate the required predictor variables. |
Lineage | Lineage includes the background information, history of the sources of data, data quality statements and methods. | River lines in the layers were derived from a Digital Rivers Network licensed from the Centre for Ecology and Hydrology (CEH). Very small rivers (First (Strahler) order rivers on the CEH digital river network) were removed from this dataset. NAs exist where we are unable to make predictions of maximum temperature, climate sensitivity or planting potential. This includes locations in lochs or in circumstances where we cannot generate the required predictor variables. The daily maximum river temperature model for Scotland is a spatio-temporal statistical model that allows current and future river temperatures and sensitivity to climate change to be predicted from; the day of the year (DoY), air temperature on that day, location in the country (region/hydrometric area), location on the river network and the characteristics of the river (elevation, bankside woodland and channel orientation). Details of the model and predictions can be found in: Jackson, F.L., Fryer, R.J., Hannah, D.M., Millar, C.P., and Malcolm, I.A. (2018) ‘A spatio-temporal statistical model of maximum daily river temperatures to inform the management of Scotland's Atlantic salmon rivers under climate change.’ Science of The Total Environment., 612, 1543-1558. (https://www.sciencedirect.com/science/article/pii/S0048969717323525?via%3Dihub=). The riparian tree planting prioritisation model is a simplified process based (deterministic) river temperature model, driven by energy gains from solar radiation, modified by coarse scale characterisation of hydrological and hydraulic conditions. Solar radiation receipt is predicted depending on channel width, orientation, aspect, gradient, tree height, tree location and solar geometry. Subsequent effects on river temperature are strongly influenced by water volume and residence time which can be broadly characterised by river order. The model compares predicted river temperatures with and without trees (ignoring energy losses) to provide a prioritisation metric, where high values indicate that tree planting can have a large effect on river temperature. The resulting output is a planting prioritisation metric that can be mapped at large spatial scales using information obtained from a digital river network to facilitate management decisions. Details of the planting prioritisation predictions can be found in: Jackson, F.L., Hannah, D.M., Ouellet, V. and Malcolm, I.A. (2021) A simplified deterministic river temperature model to prioritise the management of riparian woodland to mitigate high river temperatures under climate change (https://onlinelibrary.wiley.com/doi/abs/10.1002/hyp.14314). SRTMN national riparian woodland prioritisation scores were produced by normalising maximum temperature, climate sensitivity and planting prioritisation values between 1 and 20, summing scores across the three values and dividing by three, to give an overall prioritisation where each individual component was equally weighted. SRTMN local riparian woodland prioritisation scores were produced by rescaling prioritisation values within hydrometric areas. These scores reflect local priorities but cannot be compared between hydrometric areas. |
Related keywords | ||
Keyword | General subject area(s) associated with the resource, uses multiple controlled vocabularies | Marine Environmental Data and Information Network |
General subject area(s) associated with the resource, uses multiple controlled vocabularies | Habitat | |
General subject area(s) associated with the resource, uses multiple controlled vocabularies | Environment | |
General subject area(s) associated with the resource, uses multiple controlled vocabularies | Habitats and biotopes | |
Geographical coverage | ||
North | The northern-most limit of the data resource in decimal degrees | 60.92331 |
East | The eastern-most limit of the data resource in decimal degrees | 0.3222654 |
South | The southern-most limit of the data resource in decimal degrees | 54.53808 |
West | The western-most limit of the data resource in decimal degrees | -11.01563 |
Responsible organisations | ||
Role | The point of contact is person or organisation with responsibility for the creation and maintenance of the metadata for the resource. | pointOfContact |
Organisation name | Scottish Government (Marine Scotland) | |
Phone | +44 (0)300 244 4000 | |
Role | The point of contact is person or organisation with responsibility for the creation and maintenance of the metadata for the resource. | pointOfContact |
Organisation name | Scottish Government (Marine Scotland) | |
Phone | +44 (0)300 244 4000 | |
Delivery point | Mailpoint 11, Area 1B South, Victoria Quay | |
Postal code | EH6 6QQ | |
City | Edinburgh | |
Country | United Kingdom | |
Role | The custodian is the person or organisation that accepts responsibility for the resource and ensures appropriate care and maintenance. If a dataset has been lodged with a Data Archive Centre for maintenance then this organisation is be entered here. | custodian |
Organisation name | Scottish Government (Marine Scotland) | |
Phone | +44 (0)300 244 4000 | |
Delivery point | Mailpoint 11, Area 1B South, Victoria Quay | |
Postal code | EH6 6QQ | |
City | Edinburgh | |
Country | United Kingdom | |
Role | The distributor is the person or organisation that distributes the resource. | distributor |
Organisation name | Scottish Government (Marine Scotland) | |
Phone | +44 (0)300 244 4000 | |
Delivery point | Mailpoint 11, Area 1B South, Victoria Quay | |
Postal code | EH6 6QQ | |
City | Edinburgh | |
Country | United Kingdom | |
Role | The originator is the person or organisation who created, collected or produced the resource. | originator |
Organisation name | MARINE SCOTLAND SCIENCE FFL | |
Phone | 01312442498 | |
Delivery point | FASKALLY | |
Postal code | PH165LB | |
City | PITLOCHRY | |
Country | United Kingdom | |
Resource locators | ||
Locator URL | Web address (URL) that links to the resource | https://msmap1.atkinsgeospatial.com/geoserver/nmpwms/wms?service=wms&version=1.3.0&request=GetCapabilities |
Locator function | Code that describes the function of the resource. ISO function code chosen from ISO 19115-1 Codelist | download |
Dataset constraints | ||
Limitations on public access | Any restrictions imposed on accessing the resource such as the need to agree to certain licence conditions. | Reference must be made to the original publications: Jackson et al (2018), Jackson et al (2021). All maps must include the attribution: ‘Based on digital spatial data licensed from the Centre for Ecology & Hydrology, © NERC (CEH)' and 'Contains Ordnance Survey data © Crown copyright [year]'. |
Access constraints (code) | ISO restriction code chosen from ISO 19115-1 Codelist | otherRestrictions |
Use constraints (code) | ISO restriction name chosen from ISO 19115-1 Codelist | otherRestrictions |
Use constraints | Any restriction on the use of the resource such as the need to agree to certain licence conditions. | public access limited according to Article 13(1)(e) of the INSPIRE Directive |
Version info | ||
Date of publication | The publication date of the resource or if previously unpublished the date that the resource was made publicly available via the MEDIN network. | 2020-10-27 |
Metadata date | The date when the content of this metadata record was last updated. | 2021-10-08 |
Metadata standard name | The name of the metadata standard used to create this metadata | MEDIN Discovery Metadata |
Metadata standard version | The version of the MEDIN Discovery Metadata Standard used to create the metadata record | Version 2.3.7 |
© OpenStreetMap contributors