4.4. Lesser Black-backed gull
- Monthly estimates of collisions for the worst-case for lesser black-backed gull are presented in Table 4.10 for both the Developer and Scoping Approaches.
- The estimated number of collisions was highest during July, when monthly densities of flying lesser black-backed gulls were at their highest, with 0.13 birds/km2 (pooled SD ±0.03) and 0.18 birds/km2 (pooled SD ±0.04) respectively (Table 3.3 and Table 3.4).
- Combining the estimated mortality across bio-seasons, shows that collisions are exclusive to the breeding season (Table 4.11).
- The estimated number of collisions presented in Table 4.10 and Table 4.11 were used in population modelling reported in Technical Appendix 11.6: Ornithology Population Viability Analysis.
- Annual collision estimates for lesser black-backed gulls for all turbine scenarios and avoidance rates using the Developer and Scoping Approaches are presented in Table 4.12 and Table 4.13 respectively.
| Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec | Total |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Developer Approach | |||||||||||||
- 2 SD | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 1.02 | 6.60 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 7.62 |
Estimated number of collisions | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.85 | 5.50 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 6.35 |
+ 2 SD | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.68 | 4.40 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 5.08 |
Scoping Approach | |||||||||||||
- 2 SD | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 1.52 | 9.15 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 10.67 |
Estimated number of collisions | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 1.27 | 7.62 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 8.89 |
+ 2 SD | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 1.02 | 6.10 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 7.11 |
| Bio-season | Breeding | Non-breeding | Total |
---|---|---|---|---|
Developer Approach | Estimated collisions | 6.35 | 0.00 | 6.35 |
Scoping Approach | Estimated collisions | 8.89 | 0.00 | 8.89 |
| SNCBs Guidance | Bowgen & Cook | |||||||
---|---|---|---|---|---|---|---|---|---|
Turbine Scenario | Avoidance rate – Basic | Avoidance rate – Extended | Option 2 | Option 3 | Avoidance rate – Basic | Avoidance rate – Extended | Option 2 | Option 3 | |
Type A |
|
|
|
| |||||
14MW | 0.995 | 0.989 | 6* | 4 | 0.995 | 0.993 | 6* | 2 | |
15MW | 0.995 | 0.989 | 6* | 4 | 0.995 | 0.993 | 6* | 2 | |
18MW | 0.995 | 0.989 | 6* | 3 | 0.995 | 0.993 | 6* | 2 | |
21MW | 0.995 | 0.989 | 5 | 2 | 0.995 | 0.993 | 5 | 2 | |
24MW | 0.995 | 0.989 | 5 | 2 | 0.995 | 0.993 | 5 | 1 | |
Type B |
|
|
|
| |||||
18MW | 0.995 | 0.989 | 5 | 3 | 0.995 | 0.993 | 5 | 2 | |
21MW | 0.995 | 0.989 | 5 | 3 | 0.995 | 0.993 | 5 | 2 | |
24MW | 0.995 | 0.989 | 5 | 2 | 0.995 | 0.993 | 5 | 2 | |
*The estimated collisions for 14 MW, 15 MW and 18 MW turbines type A are 6.35, 5.57 and 6.02 per annum, respectively.
| SNCBs Guidance | Bowgen & Cook | |||||||
---|---|---|---|---|---|---|---|---|---|
Turbine Scenario | Avoidance rate – Basic | Avoidance rate – Extended | Option 2 | Option 3 | Avoidance rate – Basic | Avoidance rate – Extended | Option 2 | Option 3 | |
Type A |
|
|
|
| |||||
14MW | 0.995 | 0.989 | 9 | 5 | 0.995 | 0.993 | 9 | 3 | |
15MW | 0.995 | 0.989 | 8 | 5 | 0.995 | 0.993 | 8 | 3 | |
18MW | 0.995 | 0.989 | 8 | 4 | 0.995 | 0.993 | 8 | 3 | |
21MW | 0.995 | 0.989 | 8 | 3 | 0.995 | 0.993 | 8 | 2 | |
24MW | 0.995 | 0.989 | 7 | 3 | 0.995 | 0.993 | 7 | 2 | |
Type B |
|
|
|
| |||||
18MW | 0.995 | 0.989 | 7 | 4 | 0.995 | 0.993 | 7 | 3 | |
21MW | 0.995 | 0.989 | 7 | 4 | 0.995 | 0.993 | 7 | 2 | |
24MW | 0.995 | 0.989 | 6 | 3 | 0.995 | 0.993 | 6 | 2 | |