MODELLING SEABIRD COLLISION RISK WITH OFF-SHORE WINDFARMS
- M. Mateos, G.M. Arroyo, J.J. Alonso del Rosario
MODELLING SEABIRD COLLISION RISK WITH OFF-SHORE WINDFARMS M. Mateos, - - PowerPoint PPT Presentation
MODELLING SEABIRD COLLISION RISK WITH OFF-SHORE WINDFARMS M. Mateos, G.M. Arroyo, J.J. Alonso del Rosario Objectives To develop a stochastic model of avian collision risk at wind farms A case study To obtain Factors probabilities of
MODELLING SEABIRD COLLISION RISK WITH OFF-SHORE WINDFARMS
Objectives
Objectives
THE MODEL
CORY’S SHEARWATER Calonectris diomedea
Case study: The Strait of Gibraltar
NORTHEN GANNET Morus bassanus
Puffinus mauretanicus
Case study: The Strait of Gibraltar
Antenna 12 ft TX 3.050 MHz 286 dB 22-28 rpm 30 KW
TARIFA ISLAND Gibraltar Algeciras Ceuta
VISUAL & RADAR CENSUSES
THE MODEL: The wind farm as a risk window
RISK WINDOW
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
Number of rows: 3, 6, 9 Number of columns: 6, 10, 14 Distance between rows: 400, 700, 1000 m Distance between columns: 300, 600, 900m Distance to coast: 1, 5, 10 km
Wind farm dimensions
THE MODEL: The wind farm as a risk window
F(y)
Rows Distance to coast Columns
Flight direction Horizontal distribution of the migratory passage
THE MODEL: The wind farm as a risk window
F(y)
Montecarlo simulation
Columns Rows Distance to coast
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
Species Avoidance rate From Common Eiders WFAR 82% Desholm and Kahlert 2005
Avoidance rate
farm as a whole
Wind farm avoidance rate
Based on literature
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
Wind farm avoidance rate Random number
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
Wind farm avoidance rate Survival Survival
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR
Birds in front of a turbine: Turbine Avoidance Rate (TAR)
Left Ahead Right
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
Species
F(y)
TAR min. WFAR
Based on literature Species Avoidance rate From Common Eiders 94.6% Desholm and Kahlert 2005 Waterfowl and waders 97.5% Winkelman 1992, 1994 Gulls, waders 97% Winkelman 1985 Bewick’s Swan 99.5% Percival 2004 Gulls 99.9% Everaert et al. 2002 Common terns 99.8% Everaert et al. 2002 Barnacle, Greylag, White-fronted Geese 100% Percival 1998
Birds in front of a turbine: Turbine Avoidance Rate (TAR)
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR min. WFAR
Random number
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR
Probability of safely passing the rotor blades by chance
Following Band et al. 2007:
Birds within reach of turbine: Probability by chance (Turker 1996, Band et al. 2007)
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR
Random number
Probability of safely passing the rotor blades by chance
Birds within reach of turbine: Probability by chance (Turker 1996, Band et al. 2007)
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR
Probability of safely passing the rotor blades by chance
Survival
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR
Collision
Probability of safely passing the rotor blades by chance
THE MODEL: The wind farm as a risk window
Columns Rows Distance to coast
F(y)
TAR
Probability of safely passing the rotor blades by chance
Survival
PERCENTAGE OF MORTALITY
Objectives
Percentage of estimated collisions 0.00 0.05 0.10 0.15 0.20 0.25 Number of cases 200 400 600 800 1000 1200 1400 1600 1800 2000
13,608 scenarios: WFAR, TAR ≠ 0 94% 0 to 8 out of 10,000 birds Factors
27,216 scenarios (also WFAR, TAR = 0) 1,000,000 events per scenario
Objectives
Factors
Probability of passing safely the rotor blades by chance 1 2 3 4 Percentage of estimated collisions 0.00 0.02 0.04 0.06 0.08 0.10 0.12
Balearic Shearwater Cory's Shearwater Gannet
TAR (%) 95 96 97 98 99 Percentage of estimated collisions 0.00 0.02 0.04 0.06 0.08 0.10
) )
Number of columns
1 2 3
Percentage of estimated collisions
0.00 0.01 0.02 0.03 0.04 0.05 0.06 0.07 900 m between columns 600 m between columns 300 m between columns 6 10 14
entering passage: 18.4%
Factors
(thus confirming Desholm and Kahlert 2005, Chamberlain et al. 2006)
Percentage of birds entering the wind farm (step 0) 5 10 15 20 25 30 35 40 45 Percentage of estimated collisions 0.000 0.005 0.010 0.015 0.020 0.025
90 80 70 60 WFAR (%)
Objectives Number of birds collided per time period Bird volume Flight altitude
Estimating the mortality rates: FLIGHT ALTITUDE
FLIGHT ALTITUDE
Following Krüger and Garthe 2001, We obtained the proportion of birds flying in each height layer for:
Layer 3 Layer 2 Layer 1
Autumn migration volume in the north side of the Strait of Gibraltar
BIRD VOLUME
Percentage of Cory’s Shearwater flying at Layer 1 Layer 2 Layer 3 n E1 99.1% 0.6% 0.2% 2,160 E2 99.4% 0.6% 0.0% 36 W1 94.6% 5.3% 0.1% 3,262 W2 100.0% 0.0% 0.0% 1,195
30 4 5 Estimated number of collided birds per autumn season Estimating the mortality rates
Percentage of Balearic Shearwater flying at Layer 1 Layer 2 Layer 3 n E1 99.7% 0.3% 0.0% 1,518 E2 100.0% 0.0% 0.0% 25 W1 97.8% 2.1% 0.1% 849 W2 100% 0% 0% 20
Estimating the mortality rates 13 Estimated number of collided birds per autumn season
Percentage of Northern Gannet flying at Layer 1 Layer 2 Layer 3 n E1 90.5% 8.4% 1.1% 577 E2 97.2% 2.8% 0.0% 156 W1 76.4% 20.6% 3.0% 718 W2 91.2% 8.3% 0.6% 223
3 Estimating the mortality rates Estimated number of collided birds per autumn season
Conclusions: THE CASE STUDY
Conclusions: THE MODEL