Gannet

  1. 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.
  2. 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.

 

Table 4.18: Potential gannet mortality following displacement from the Berwick Bank Development array 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)

Displacement Level

(% of all birds on site)

 

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)

Displacement Level

(% of all birds on site)

 

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)

Displacement Level

(% of all birds on site)

 

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

Table 4.21: Potential gannet mortality following displacement from the Berwick Bank Development array plus 2 km buffer in the spring migration (non-breeding) period. 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

 

(Spring migration)

Mortality Level

(% of displaced birds at risk of mortality)

Displacement Level

(% of all birds on site)

 

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

Table 4.22: Potential gannet mortality following displacement from the Berwick Bank Development array plus 2 km buffer in the autumn migration (non-breeding) period. 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

 

(Autumn migration)

Mortality Level

(% of displaced birds at risk of mortality)

Displacement Level

(% of all birds on site)

 

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