Annex C Auk Displacement Mortality for the Berwick Bank Development Array plus 2km buffer: SPATIAL Approach

  1. For context, the Applicant has used the Matrix method, to explore outputs based on different displacement rates applied spatially (“Spatial Approach”) across the Array area and buffer. The approach has been applied to auks, and area-specific displacement rates applied within the 2km buffer and the Development Array (see ‘Spatial Approach” in Table 3.4).
  1. Matrices for the ‘2km buffer only’ were formulated by subtracting the matrices for the Development Array from the matrices for the Development Array plus 2km buffer (displayed in sections 0 to 0) and are presented below in Table C.1 to Table C.6.
  2. The outputs highlighted in colour are those deemed the ‘most realistic’ mortality estimates, based on the displacement and mortality rates as advised by the: i) Scoping Opinion (highlighted in dark teal; rates outlined in Table 3.4) and ii) the “Spatial Approach” (highlighted in orange). For the Spatial Approach, the Developer uses a displacement rate of 30% and mortality rate of 1% for all auk species in all seasons within the 2km buffer. Cells highlighted in light teal outline the potential associated uncertainty around these figures.
  3. The figures highlighted in orange from the Development Array matrices based on a displacement rate of 50% and mortality rate of 1% for all auk species in all season) and the 2km buffer only matrices were then summed to get the final mortality values across the Development Array plus 2km buffer with regards to the Spatial Approach. These are displayed in Table C.7 along with the outputs from the Developer Approach for comparison.

Table C.1: Potential guillemot mortality in the 2km buffer only, 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; orange representing rates defined by the Spatial Approach; and light teal representing uncertainty around these figures.

Guillemot

 

(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

15

29

43

58

72

145

217

290

434

723

1157

1447

20%

0

29

58

86

116

145

290

434

579

868

1447

2314

2893

30%

0

43

86

130

173

217

434

650

868

1301

2170

3471

4339

40%

0

58

116

173

231

290

579

868

1157

1736

2893

4629

5786

50%

0

72

145

217

290

361

723

1085

1447

2170

3616

5786

7232

60%

0

86

173

260

347

434

868

1301

1736

2603

4339

6942

8678

70%

0

102

203

304

405

506

1012

1519

2025

3038

5062

8100

10124

80%

0

116

231

347

462

579

1157

1736

2314

3471

5786

9257

11572

90%

0

130

260

391

521

650

1301

1952

2603

3905

6509

10414

13018

100%

0

145

290

434

579

723

1447

2170

2893

4340

7232

11572

14464

Table C.2: Potential guillemot mortality in the 2km buffer only, 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; orange representing rates defined by the Spatial Approach; and light teal representing uncertainty around these figures.

Guillemot

 

(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

10

20

30

40

50

101

152

203

304

507

810

1014

20%

0

20

40

61

81

101

203

304

405

608

1014

1621

2027

30%

0

30

61

91

122

152

304

456

608

912

1520

2432

3040

40%

0

40

81

122

162

203

405

608

810

1216

2027

3242

4053

50%

0

50

101

152

203

254

507

760

1014

1520

2533

4053

5067

60%

0

61

122

183

244

304

608

912

1216

1824

3040

4864

6080

70%

0

71

142

213

283

354

709

1064

1418

2128

3546

5674

7093

80%

0

81

162

244

324

405

810

1216

1621

2432

4053

6485

8106

90%

0

91

183

273

365

456

912

1368

1824

2736

4559

7296

9119

100%

0

101

203

304

405

507

1014

1520

2027

3040

5067

8106

10133

Table C.3: Potential razorbill mortality in the 2km buffer only, 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; orange representing rates defined by the Spatial Approach; and light teal representing uncertainty around these figures.

Razorbill

 

(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

1

2

3

4

5

10

15

20

30

49

80

99

20%

0

2

4

6

8

10

20

30

40

60

99

160

199

30%

0

3

6

9

12

15

30

45

60

90

150

239

300

40%

0

4

8

12

16

20

40

60

80

119

199

319

399

50%

0

5

10

15

20

24

49

74

99

149

249

399

499

60%

0

6

12

18

23

30

60

90

119

180

300

479

599

70%

0

7

14

21

28

35

70

105

140

210

350

559

699

80%

0

8

16

23

32

40

80

119

160

239

399

639

798

90%

0

9

18

27

36

45

90

135

180

269

449

718

898

100%

0

10

20

30

40

49

99

149

199

299

499

798

998


Table C.4: Potential razorbill mortality in the 2km buffer only, 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; orange representing rates defined by the Spatial Approach; and light teal representing uncertainty around these figures.

Razorbill

 

(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

4

7

11

15

18

36

55

73

109

181

291

363

20%

0

7

15

22

29

36

73

109

146

218

363

582

727

30%

0

11

22

33

44

55

109

164

218

328

545

873

1091

40%

0

15

29

44

58

73

146

218

291

437

727

1163

1455

50%

0

18

36

55

73

90

181

272

363

545

909

1455

1819

60%

0

22

44

66

87

109

218

328

437

655

1091

1746

2182

70%

0

25

51

76

102

127

255

382

509

764

1273

2037

2546

80%

0

29

58

87

116

146

291

437

582

873

1455

2327

2910

90%

0

33

66

98

131

164

328

491

655

982

1637

2619

3274

100%

0

36

73

109

146

181

363

545

727

1091

1819

2910

3637

Table C.5: Potential puffin mortality in the 2km buffer only, 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; orange representing rates defined by the Spatial Approach; and light teal representing uncertainty around these figures.

Puffin

 

(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

1

3

3

5

6

12

17

23

34

56

90

113

20%

0

3

5

7

9

12

23

34

45

67

113

180

225

30%

0

3

7

10

14

17

34

51

67

101

168

270

336

40%

0

5

9

14

18

23

45

67

90

135

225

360

450

50%

0

6

12

17

23

28

56

84

113

168

281

450

562

60%

0

7

14

20

27

34

67

101

135

202

336

539

673

70%

0

8

16

23

32

39

78

118

157

236

393

629

787

80%

0

9

18

27

36

45

90

135

180

270

450

719

899

90%

0

10

20

30

40

51

101

152

202

303

505

809

1011

100%

0

12

23

34

45

56

113

168

225

337

562

899

1123

 

Table C.6: Potential puffin mortality in the 2km buffer only, 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; orange representing rates defined by the Spatial Approach; and light teal representing uncertainty around these figures.

Puffin

 

(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

5

6

7

14

21

28

43

71

114

142

20%

0

3

6

9

12

14

28

43

57

86

142

228

285

30%

0

5

9

13

17

21

43

64

86

128

214

342

428

40%

0

6

12

17

23

28

57

86

114

171

285

456

570

50%

0

7

14

21

28

35

71

106

142

213

356

570

712

60%

0

9

17

25

34

43

86

128

171

257

428

684

855

70%

0

10

20

30

40

50

99

150

199

299

499

798

998

80%

0

12

23

34

46

57

114

171

228

342

570

912

1140

90%

0

13

25

39

51

64

128

192

257

384

641

1026

1282

100%

0

14

28

43

57

71

142

213

285

427

712

1140

1425

Table C.7: Potential auk mortality per bio-season following displacement and barrier effects from the Berwick Bank Development array plus 2km buffer, for the Spatial Approach and Spatial Approach mortality and displacement rates listed under the Spatial Approach in Table 3.5.

Species

Developer Approach

 

Spatial Approach

 

 

Breeding

season

Non-breeding season

Breeding

season

Non-breeding season

Developer Approach

 

 

 

 

Guillemot

371

221

342

201

Razorbill

21

62

19

55

Puffin

34

N/A

20

N/A