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Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

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Page 1: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Bob BattyScottish Association for Marine

Science

Impact Assessment: predictive modelling of collision risk

Page 2: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Impact Assessment:Predictive Modelling of Collision

Risk

Bob Batty

Scottish Association For Marine Science

Page 3: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Collision Risk

• How often will animals collide with turbines?– Use Encounter Models adapted from behavioural ecology to

predict encounter rate Z

• But animals may detect and avoid encounter (at some distance), evade collision (at close range) or even be attracted

• Is the passive encounter rate sufficient to have to consider animal behaviour?

• Can we predict avoidance A and evasion E?• Collision Rate = Z (1-E) (1-A)

Page 4: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Encounter

Encounter

But not an Encounter

At SAMS, encounter models developed for behavioural ecology have been adapted to predict encounter rates between animals and turbines.

Page 5: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Encounter Rate/Riskand Animal Size

Expected encounter rate declines with increasing body size – fewer larger animals.

But as a proportion of the population encounters are much greater: a relative “Risk” estimate.

0.00000001

0.0000001

0.000001

0.00001

0.0001

0.001

0.01

0.1

1

10

100

1000

0.01 0.1 1 10

Animal Size, Body Length (m)

Enc

ount

er r

ate

z (

.s-1

)1

10

100

Rel

ativ

e R

isk

encounter rate Z

"Risk" (Z/density)

100 turbines 20 m in diameter to the west of Scotland could result in encounters with 2% of the herring population and 10% of the harbour porpoise population per annum.

Real values will be less due to AVOIDANCE or greater due to ATTRACTIONAnd EVASION will reduce collisions during encounters.

Page 6: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Avoidance

Avoidance

SAMS has developed an acoustic detection model to predict the distance upstream at which species may detect a device above background noise levels and also developed equipment to measure background noise level.

Page 7: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Evasion

Evasion

A visual stimulus evasion model has been developed at SAMS for fish. An acoustic model can be developed. Both may be extended to include mammals.

Page 8: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Evasion - Visual Response

• Ability to evade collision depends on:– Looming rate of turbine blade and True

Looming Threshold (TLT)– Latency– C-start escape orientation distribution– Burst swimming performance

• animal length• temperature (for fish and invertebrates only)

Page 9: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Evasion - Visual Response

The Effect of Fish Size on evasion

Evasion depends on fish size, temperature and blade thickness.Evasion by fish and invertebrates less likely at lower temperature

– a seasonal and location effect.

Blade thickness 30 cmTemperature 10°C

0

0.2

0.4

0.6

0.8

1

p E

vasi

on

Blade Velocity m s-1

FishLength

m00.2

0.40.6

0.81

46

1012

1416

02

8

0.8-1

0.6-0.8

0.4-0.6

0.2-0.4

0-0.2

Page 10: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

Blade Thickness and Velocity

For a fish with a total length of 30 cm at 10°C

0.2

0.4

0

0.2

0.4

0.6

0.8

1p

Eva

sio

n

Blade Velocity m s-1blade

thicknessm

0.8-1

0.6-0.8

0.4-0.6

0.2-0.4

0-0.2

46

1012

1416

02

80.6

but thinner blades are not better!

Page 11: Bob Batty Scottish Association for Marine Science Impact Assessment: predictive modelling of collision risk

Scottish Marine Institute,Oban, ArgyllPA37 1QAScotland, UK

0

2

4

6

8

10

12

14

16

2 3 4 5 6 7

Killer Whale Body Length (m)

Velo

city

(m

.s-1)

Lunges (max) Lunges (average)

Tail slaps herring

Evasion not possible at similar fluke velocities to maximum turbine blade tip velocities of some turbines

Maximum blade velocity

Killer Whale “Carousel feeding” on herringFits model predictions well

Domenici, Batty, Simila, Ogam (2000). Journal of Expeimental Biology, 203, 283-294.