Gannet
- In addition to the Matrix method, GPS tracking data of gannets from the Bass Rock colony 2010 - 2019 were analysed to contribute to understanding how the proposed Project may lead to displacement and barrier effects on this colony population. Data from breeding adults from Bass Rock were used to estimate behavioural states using Hidden Markov Models, and the proportion of time spent in each behavioural state and within and outwith the windfarm, split by sex. The analysis demonstrates the extensive spatial range of gannets from the colony and showed that males spent on average 10.5% less time transiting than females across all trips. When sex and behaviour were considered within the Development Array are only, males spent on average 38% more time foraging within the area than females.
- Random resampling of the dataset using size of the Development Array area was used to explore the distribution of the data and whether there was evidence of it being used preferentially to other equivalently sized areas. The number of observations counted out of 863 samples of the dataset, showed that the proposed Development Array area had a higher count than 94% of the samples. However, this resampling does not account for proximity to colony or landmasses. Annex E details analysis of GPS tracks of gannet tracked from Bass rock in the Forth and Tay. It was found that of the 682 birds tracked, only 26.2% of those individuals entered the development area, and of those only 52.5% (94 birds) engaged in any foraging activities (see table 3.3). Figure 3.3 illustrates the locations of predicted foraging behaviour (as identified by hidden Markov modelling) and that due to the large home ranges (median 3,909 km2), most foraging activity occurs outside the development site.
Gannet
(Breeding season) | Mortality Level (% of displaced birds at risk of mortality) | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 0% | 1% | 2% | 3% | 4% | 5% | 10% | 15% | 20% | 30% | 50% | 80% | 100% | |
0% | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | |
10% | 0 | 4 | 8 | 11 | 15 | 18 | 36 | 54 | 72 | 108 | 179 | 286 | 358 | |
20% | 0 | 8 | 15 | 22 | 29 | 36 | 72 | 108 | 143 | 215 | 358 | 572 | 715 | |
30% | 0 | 11 | 22 | 33 | 43 | 54 | 108 | 161 | 215 | 322 | 536 | 858 | 1072 | |
40% | 0 | 15 | 29 | 43 | 58 | 72 | 143 | 215 | 286 | 429 | 715 | 1144 | 1429 | |
50% | 0 | 18 | 36 | 54 | 72 | 90 | 179 | 268 | 358 | 536 | 893 | 1429 | 1786 | |
60% | 0 | 22 | 43 | 65 | 86 | 108 | 215 | 322 | 429 | 643 | 1072 | 1715 | 2144 | |
70% | 0 | 26 | 51 | 76 | 101 | 126 | 251 | 376 | 501 | 751 | 1251 | 2001 | 2501 | |
80% | 0 | 29 | 58 | 86 | 115 | 143 | 286 | 429 | 572 | 858 | 1429 | 2287 | 2858 | |
90% | 0 | 33 | 65 | 97 | 129 | 161 | 322 | 483 | 643 | 965 | 1608 | 2572 | 3215 | |
100% | 0 | 36 | 72 | 108 | 143 | 179 | 358 | 536 | 715 | 1072 | 1786 | 2858 | 3572 |
Table 4.19: Potential gannet mortality following displacement from the Berwick Bank Development Array plus 2 km buffer in the breeding season. Estimates considered, in light of empirical evidence, to represent the most realistic scenarios are colour coded, with dark teal representing rates advised by the Scoping Opinion; dark teal and orange coloured hatching representing overlapping estimates from both the Scoping Opinion and Developer Approach.; and light teal representing uncertainty around these figures.
Gannet
(Breeding season) | Mortality Level (% of displaced birds at risk of mortality) | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 0% | 1% | 2% | 3% | 4% | 5% | 10% | 15% | 20% | 30% | 50% | 80% | 100% | |
0% | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | |
10% | 0 | 5 | 10 | 15 | 19 | 24 | 48 | 72 | 95 | 143 | 237 | 379 | 474 | |
20% | 0 | 10 | 19 | 29 | 38 | 48 | 95 | 143 | 190 | 285 | 474 | 758 | 947 | |
30% | 0 | 15 | 29 | 43 | 57 | 72 | 143 | 214 | 285 | 427 | 711 | 1137 | 1421 | |
40% | 0 | 19 | 38 | 57 | 76 | 95 | 190 | 285 | 379 | 569 | 947 | 1516 | 1894 | |
50% | 0 | 24 | 48 | 72 | 95 | 119 | 237 | 356 | 474 | 711 | 1184 | 1894 | 2368 | |
60% | 0 | 29 | 57 | 86 | 114 | 143 | 285 | 427 | 569 | 853 | 1421 | 2273 | 2842 | |
70% | 0 | 34 | 67 | 100 | 133 | 166 | 332 | 498 | 663 | 995 | 1658 | 2652 | 3315 | |
80% | 0 | 38 | 76 | 114 | 152 | 190 | 379 | 569 | 758 | 1137 | 1894 | 3031 | 3788 | |
90% | 0 | 43 | 86 | 128 | 171 | 214 | 427 | 640 | 853 | 1279 | 2131 | 3410 | 4262 | |
100% | 0 | 48 | 95 | 143 | 190 | 237 | 474 | 711 | 947 | 1421 | 2368 | 3788 | 4735 |
Table 4.20: Potential gannet mortality following displacement from the Berwick Bank Development Array in the non-breeding season. Estimates considered, in light of empirical evidence, to represent the most realistic scenarios are colour coded, with dark teal representing rates advised by the Scoping Opinion; dark teal and orange coloured hatching representing overlapping estimates from both the Scoping Opinion and Developer Approach.; and light teal representing uncertainty around these figures.
Gannet
(Non-breeding season) | Mortality Level (% of displaced birds at risk of mortality) | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 0% | 1% | 2% | 3% | 4% | 5% | 10% | 15% | 20% | 30% | 50% | 80% | 100% | |
0% | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | |
10% | 0 | 2 | 3 | 4 | 5 | 6 | 11 | 16 | 21 | 31 | 51 | 82 | 102 | |
20% | 0 | 3 | 5 | 7 | 9 | 11 | 21 | 31 | 41 | 62 | 102 | 164 | 204 | |
30% | 0 | 4 | 7 | 10 | 13 | 16 | 31 | 46 | 62 | 92 | 153 | 245 | 306 | |
40% | 0 | 5 | 9 | 13 | 17 | 21 | 41 | 62 | 82 | 123 | 204 | 327 | 408 | |
50% | 0 | 6 | 11 | 16 | 21 | 26 | 51 | 77 | 102 | 153 | 255 | 408 | 510 | |
60% | 0 | 7 | 13 | 19 | 25 | 31 | 62 | 92 | 123 | 184 | 306 | 490 | 612 | |
70% | 0 | 8 | 15 | 22 | 29 | 36 | 72 | 107 | 143 | 214 | 357 | 571 | 714 | |
80% | 0 | 9 | 17 | 25 | 33 | 41 | 82 | 123 | 164 | 245 | 408 | 653 | 816 | |
90% | 0 | 10 | 19 | 28 | 37 | 46 | 92 | 138 | 184 | 276 | 459 | 734 | 918 | |
100% | 0 | 11 | 21 | 31 | 41 | 51 | 102 | 153 | 204 | 306 | 510 | 816 | 1019 |
Gannet
(Spring migration) | Mortality Level (% of displaced birds at risk of mortality) | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 0% | 1% | 2% | 3% | 4% | 5% | 10% | 15% | 20% | 30% | 50% | 80% | 100% | |
0% | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | |
10% | 0 | 0 | 1 | 1 | 1 | 1 | 3 | 4 | 5 | 8 | 13 | 22 | 27 | |
20% | 0 | 1 | 1 | 2 | 2 | 3 | 5 | 8 | 11 | 16 | 27 | 43 | 54 | |
30% | 0 | 1 | 2 | 2 | 3 | 4 | 8 | 12 | 16 | 24 | 40 | 65 | 81 | |
40% | 0 | 1 | 2 | 3 | 4 | 5 | 11 | 16 | 22 | 32 | 54 | 86 | 108 | |
50% | 0 | 1 | 3 | 4 | 5 | 7 | 13 | 20 | 27 | 40 | 67 | 108 | 134 | |
60% | 0 | 2 | 3 | 5 | 6 | 8 | 16 | 24 | 32 | 48 | 81 | 129 | 161 | |
70% | 0 | 2 | 4 | 6 | 8 | 9 | 19 | 28 | 38 | 56 | 94 | 151 | 188 | |
80% | 0 | 2 | 4 | 6 | 9 | 11 | 22 | 32 | 43 | 65 | 108 | 172 | 215 | |
90% | 0 | 2 | 5 | 7 | 10 | 12 | 24 | 36 | 48 | 73 | 121 | 194 | 242 | |
100% | 0 | 3 | 5 | 8 | 11 | 13 | 27 | 40 | 54 | 81 | 134 | 215 | 269 |
Gannet
(Autumn migration) | Mortality Level (% of displaced birds at risk of mortality) | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 0% | 1% | 2% | 3% | 4% | 5% | 10% | 15% | 20% | 30% | 50% | 80% | 100% | |
0% | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | |
10% | 0 | 2 | 3 | 4 | 6 | 8 | 15 | 22 | 30 | 45 | 75 | 120 | 150 | |
20% | 0 | 3 | 6 | 9 | 12 | 15 | 30 | 45 | 60 | 90 | 150 | 240 | 300 | |
30% | 0 | 5 | 9 | 14 | 18 | 23 | 45 | 68 | 90 | 135 | 225 | 360 | 450 | |
40% | 0 | 6 | 12 | 18 | 24 | 30 | 60 | 90 | 120 | 180 | 300 | 480 | 600 | |
50% | 0 | 8 | 15 | 22 | 30 | 38 | 75 | 112 | 150 | 225 | 375 | 600 | 750 | |
60% | 0 | 9 | 18 | 27 | 36 | 45 | 90 | 135 | 180 | 270 | 450 | 720 | 900 | |
70% | 0 | 11 | 21 | 32 | 42 | 53 | 105 | 158 | 210 | 315 | 525 | 840 | 1050 | |
80% | 0 | 12 | 24 | 36 | 48 | 60 | 120 | 180 | 240 | 360 | 600 | 960 | 1200 | |
90% | 0 | 14 | 27 | 40 | 54 | 68 | 135 | 202 | 270 | 405 | 675 | 1080 | 1350 | |
100% | 0 | 15 | 30 | 45 | 60 | 75 | 150 | 225 | 300 | 450 | 750 | 1200 | 1500 |