Scottish Marine and Freshwater Science Volume 5 Number 8: EMEC Billia Croo Wave Test Site: Wildlife Observations Project Annual Report
Annual report of the wildlife observation programme underway at the European Marine Energy Centre (EMEC) in Orkney.
4. Project Summary
4.1 Site Activity
A number of developers have completed various stages of device installation at the test site during the period 01 April 2013 to 31 March 2014. Table 1 below summarises work in progress during this period.
Table 1: Developer site activity at the EMEC Billia Croo test site 1st April 2013 to 31st March 2014
EMEC Berth | Developer | Activity |
---|---|---|
1 | E.ON | No activity |
2 | Scottish Power Renewables | Device testing |
3 | Vacant | No activity |
4 | Seatricity | Installation activity |
5 | Wello Oy | Installation activity |
Shallow water | Aquamarine Power Ltd | Device testing |
Installed devices may or may not be operational at any given time. Additional activity at the test site may include periodic complete removal/re-installation of devices for maintenance, maintenance visits by developers, deployment of Acoustic Doppler Current Profilers to measure resource, and acoustic surveys.
4.2 Project Activity
Overall, this contract period has seen a very high completion rate of planned watches, with an average watch achievement rate of 92%.
The third quarter of the contract suffered a reduced rate of data collection due to the exceptionally heavy storms which were a persistent feature of the UK and Orkney weather pattern in winter 2013/14. The reduced daylight hours experienced in Orkney during the winter months afford less flexibility in the schedule. Nevertheless, watch achievement rates remained above 75% for all months (see Table 2 below).
Table 2: Achievement of watches expressed as a percentage and actual contractual hours per month.
Month | Percentage (%) | Actual/Potential Hours | Comments |
---|---|---|---|
April 2013 | 100 | 80/80 | |
May 2013 | 100 | 80/80 | |
June 2013 | 95 | 76/80 | Bad weather |
July 2013 | 100 | 80/80 | |
August 2013 | 100 | 80/80 | |
September 2013 | 100 | 80/80 | |
October 2013 | 100 | 80/80 | |
November 2013 | 80 | 64/80 | Bad weather |
December 2013 | 75 | 60/80 | Bad weather |
January 2014 | 85 | 68/80 | Bad weather |
February 2014 | 75 | 60/80 | Bad weather |
March 2014 | 98 | 78/80 | Bad weather |
A new set of "Big Eyes" binoculars, with exactly the same specification as the previous set, were installed at the end of March 2014. This was required as the current set were showing significant signs of wear. The possibility of sourcing a unit with a better inclination angle measurement system and a built-in range finding system was explored, but there is currently nothing available that would meet this requirement.
4.3 Wildlife Observations Summary
Detailed analysis of the data collected is out-with the scope of this project. The entire set of raw wildlife observation data collected for the period 1 April 2013 to 31 March 2014 will be available to download from the Marine Scotland Interactive website.
The monthly wildlife sighting counts are presented in Table 3 and Table 4 below. Note these sightings are total sightings per month, and have not been corrected for effort (number of hours observed per month). The high number of unidentified seals sighted in August 2013 is due to increased seal sightings further offshore during that month. Seasonal graphs showing sighting counts per mean summer month and per mean winter month are also provided (Figures 2 to 4).
Monthly wildlife sighting counts with respect to monthly means (calculated from the entire EMEC Wildlife Observations Programme Billia Croo dataset) are presented graphically in Annex B.
Table 3: Monthly sighting counts for bird species for period April 2013 to March 2014 at the EMEC Billia Croo wave test site.
Species | Apr-13 | May-13 | Jun-13 | Jul-13 | Aug-13 | Sep-13 | Oct-13 | Nov-13 | Dec-13 | Jan-14 | Feb-14 | Mar-14 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
Arctic skua | 0 | 1 | 6 | 26 | 3 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Arctic tern | 0 | 4 | 64 | 75 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Black guillemot | 374 | 136 | 145 | 157 | 66 | 10 | 94 | 11 | 5 | 49 | 138 | 270 |
Black headed gull | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Black scoter | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Black throated diver | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Common gull | 0 | 0 | 0 | 0 | 1 | 0 | 8 | 42 | 0 | 0 | 0 | 10 |
Common guillemot | 378 | 337 | 314 | 1478 | 8 | 21 | 70 | 31 | 37 | 88 | 135 | 176 |
Common scoter | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 9 | 0 | 0 | 0 | 0 |
Cormorant | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Diver Sp. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Eider Duck | 142 | 18 | 9 | 37 | 63 | 48 | 42 | 99 | 86 | 144 | 185 | 86 |
Fulmer | 2049 | 821 | 1224 | 1954 | 1562 | 1970 | 271 | 469 | 715 | 2108 | 535 | 1759 |
Gannet | 258 | 358 | 101 | 72 | 390 | 283 | 249 | 103 | 26 | 22 | 20 | 14 |
Glaucous gull | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Goldeneye | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Goosander | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Greater black-backed gull | 24 | 10 | 16 | 5 | 12 | 5 | 30 | 80 | 102 | 68 | 78 | 39 |
Great northern diver | 1 | 1 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 10 | 20 | 15 |
Great skua | 13 | 144 | 151 | 90 | 103 | 41 | 14 | 0 | 0 | 0 | 0 | 0 |
Grey phalarope | 0 | 0 | 0 | 0 | 0 | 3 | 3 | 0 | 0 | 0 | 0 | 0 |
Geylag goose | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Herring gull | 40 | 2 | 5 | 14 | 9 | 3 | 92 | 35 | 61 | 25 | 35 | 32 |
Icelandic gull | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | 1 | 0 | 2 | 0 |
Kittiwake | 14 | 83 | 322 | 70 | 0 | 0 | 14 | 20 | 3 | 4 | 1 | 18 |
Leach's petrel | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Lesser black-backed gull | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Little Auk | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 1 | 0 | 4 | 4 | 2 |
Long tailed duck | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 1 | 2 | 2 | 0 | 4 |
Mallard | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Manx shearwater | 0 | 9 | 6 | 33 | 0 | 5 | 0 | 0 | 0 | 0 | 0 | 0 |
Mew gull | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Northern shoveler | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Phalacrocorax Sp. | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Puffin | 45 | 91 | 191 | 438 | 15 | 0 | 0 | 0 | 0 | 0 | 2 | 13 |
Razorbill | 23 | 70 | 34 | 98 | 0 | 0 | 0 | 0 | 0 | 0 | 3 | 15 |
Red breasted merganser | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Red throated diver | 3 | 4 | 3 | 0 | 0 | 0 | 0 | 2 | 0 | 2 | 0 | 0 |
Sabine's gull | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Sandwich tern | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Scaup | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Shag | 747 | 492 | 534 | 658 | 865 | 1021 | 1069 | 695 | 306 | 434 | 401 | 457 |
Shelduck | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Slavonian grebe | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Storm petrel | 0 | 1 | 6 | 3 | 1 | 3 | 0 | 0 | 0 | 0 | 0 | 0 |
Surf scoter | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Teal | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Unidentified auk | 122 | 264 | 242 | 795 | 57 | 9 | 32 | 17 | 13 | 32 | 94 | 119 |
Unidentified duck | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Unidentified goose | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Unidentified gull | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 5 | 0 |
Unidentified tern | 34 | 103 | 169 | 197 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Unidentified bird | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Velvet scoter | 0 | 0 | 0 | 0 | 0 | 0 | 8 | 0 | 0 | 0 | 0 | 0 |
Wigeon | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Total Birds | 4267 | 2949 | 3544 | 6200 | 3155 | 3422 | 2003 | 1620 | 1357 | 2992 | 1658 | 3029 |
Table 4: Monthly sighting counts for seals, cetaceans and other species for period April 2013 to March 2014 at the EMEC Billia Croo tidal test site.
Species | Apr-13 | May-13 | Jun-13 | Jul-13 | Aug-13 | Sep-13 | Oct-13 | Nov-13 | Dec-13 | Jan-14 | Feb-14 | Mar-14 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
Harbour seal | 1 | 0 | 0 | 4 | 0 | 0 | 0 | 0 | 1 | 1 | 0 | 0 |
Grey seal | 5 | 5 | 20 | 189 | 22 | 18 | 40 | 10 | 9 | 2 | 2 | 8 |
Unidentified seal | 2 | 1 | 0 | 0 | 33 | 6 | 19 | 2 | 7 | 4 | 2 | 1 |
TOTAL SEALS | 8 | 6 | 20 | 193 | 55 | 24 | 59 | 12 | 17 | 7 | 4 | 9 |
Harbour porpoise | 12 | 10 | 6 | 28 | 22 | 7 | 12 | 5 | 3 | 3 | 4 | 4 |
Humpback whale | 0 | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 |
Minke whale | 0 | 5 | 7 | 2 | 3 | 3 | 2 | 0 | 0 | 0 | 0 | 1 |
Bottlenose dolphin | 4 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
White beaked dolphin | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
White-sided dolphin | 6 | 2 | 0 | 0 | 2 | 0 | 7 | 0 | 0 | 0 | 0 | 0 |
Risso's dolphin | 4 | 4 | 6 | 7 | 0 | 10 | 6 | 0 | 3 | 8 | 4 | 0 |
Short-beaked common dolphin | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Long-finned pilot whale | 0 | 0 | 27 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Pilot whale | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Orca | 0 | 12 | 11 | 0 | 16 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Unidentified cetacean | 8 | 9 | 0 | 0 | 22 | 3 | 2 | 1 | 0 | 4 | 1 | 4 |
TOTAL CETACEANS | 34 | 42 | 57 | 37 | 65 | 24 | 29 | 6 | 6 | 15 | 9 | 9 |
Basking shark | 0 | 4 | 1 | 1 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 |
Otter (Euoropean) | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
Figures 2 to 4 below summarise the species of birds, cetaceans and seals observed at the Billia Croo tidal test site during summer (April to September) and winter (October to March) months. Values shown are mean summer month (red) and mean winter month (blue). Any inter-seasonal comparisons drawn from figures 2 to 4 should be made with caution as the data represents only one year of observations.
Figure 2: Mean summer month (red) and mean winter month (blue) bird species sightings at the Billia Croo for period April 2013 to March 2014.
Figure 3: Mean summer month (red) and mean winter month (blue) seal species sightings at the Billia Croo for period April 2013 to March 2014.
Figure 4: Mean summer month (red) and mean winter month (blue) cetacean, basking shark and otter species sightings at the Billia Croo for period April 2013 to March 2014.
4.4 Issues & Concerns
Under a separate project funded by Marine Scotland and SNH, EMEC will undertake detailed analysis of the data gathered through this project. Within the data analysis project, EMEC has sought expert input from the Centre for Research into Ecological and Environmental Modelling ( CREEM) who have identified a limitation with the data in that there is insufficient data to construct 'detection functions' for the test sites.
To address this limitation, EMEC has developed a proposal for a boat-based calibration exercise to collect additional wildlife observation data at the test sites. This would provide information about the detectability rates for a range of distances from the observation points. The steering group for the data analysis project (which comprises Marine Scotland, SNH and EMEC) agree that the construction of site-specific detection functions, which will enable modelling of absolute changes in surface-visible wildlife presence, is an important output of the analysis project.
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