Open Government Licence (OGL)

What is it: 

The spawning grounds of haddock (Melanogrammus aeglefinus) layer has been generated to identify the likely distribution of haddock spawning in the North Sea and West of Scotland, taking account of certain environmental influences. The map key refers to mean values, where a value of 0 indicates ‘low’ prediction of preference as a spawning ground and a value of 1 as a ‘high’ prediction of preference.  

This layer updates the existing (Coull et al., 1998) spawning map for haddock (Melanogrammus aeglefinus) also available on NMPi, by providing finer granularity to the likely haddock spawning areas. The Coull et al., (1998) maps have been used for more than a decade to ensure that appropriate protection is afforded to sensitive areas from disturbance.

The model used to create the layers was designed for use at a regional level and above.

More Information: 

Data was obtained from two surveys; the North Sea International Bottom Trawl Survey (NS-BTS) and the Scottish West Coast Bottom Trawl Survey (SWC-IBTS) to assess the abundance of haddock in spawning stage (HSS) (2009 – 2015). The importance of environmental influences on spawning distribution was then examined using General Additive Models (GAMs). Environmental variables such as water depth, distance to coast, springtide (tidal currents), sediment type, temperature and salinity were considered.

An optimum temperature for spawning of 7⁰C was evident for North Sea and west of Scotland regions. Spawning haddock preferred high salinity waters in the northern North Sea and shelf edge waters to the west of Scotland. They tended not to aggregate on mud-rich sediments, which was associated with a split in the main spawning areas between the east and west North Sea. The distribution of spawning haddock from this study indicated a shift in the spawning grounds compared to historic reports. By identifying the physical characteristics and persistent use of spawning grounds, the present study provides a guide for future marine developments and an aid to discussions about the utility of spawning closures.

This output serves as an update to the existing (Coull et al., 1998) spawning map for haddock (Melanogrammus aeglefinus) also available on NMPi, by providing finer granularity to the likely haddock spawning areas.

Publication DOI: https://doi.org/10.1016/j.fishres.2016.05.028

Waste water treatment is designed to process waste water whilst protecting the environment and maintaining public health. Outfalls to the marine environment fall into three categories:

1. outfalls from waste water treatment (WWT) plants which process waste water from the mains sewerage system  (this layer);
2. industrial sites which take waste from manufacturing plants (see separate layer - Industrial (SPRI) marine discharges); and
3. some private domestic sources (not on NMPi).

These categories of outfall also discharge to the riverine freshwater environment which eventually reach the sea.

The Scottish Pollutant Release Inventory (SPRI) is a database of annual mass releases of specified pollutants to air, water and land from SEPA regulated industrial sites. It also provides information about off-site transfers of waste from these sites. The SPRI will provide emission values and waste transfers when they are over the reporting thresholds and indicate if a site releases a pollutant below the threshold. From 2007, SPRI data has been used to fulfill the reporting requirements of the European Pollutant Release and Transfer Register (E-PRTR).

This data has been filtered by SEPA to include only discharges to marine environment.

The Areas of Search and exclusions identify early Sectoral Marine Planning considerations for suitable offshore wind development. These locations will be progressed through a Sectoral Marine Planning exercise to determine areas of seabed, that can be leased by Crown Estate Scotland, for offshore wind projects that will be replacing traditional energy sources for oil and gas platforms/infrastructure. Following a public consultation (August 2022 to October 2022) the areas have been modified and republished in the INTOG Initial Plan Framework (February 2022)