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Perspectives on Impacts of Land-based Wind Energy Development in New England New England Wind E nergy Education Project Conference and Workshop Marlborough, MA 7 June 2011 Carol R. Foss New Hampshire Audubon
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Page 1: Carol Foss Slides 6.7.11

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Perspectives on Impacts of Land-based

Wind Energy Developmentin New England

New England Wind Energy Education ProjectConference and Workshop

Marlborough, MA

7 June 2011

Carol R. FossNew Hampshire Audubon

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Direct vs. Indirect Impacts

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Direct Impacts

• Impact type: Mortality

• Mechanism: Collisions with turbines

• Affected organisms: Birds and bats• Documentation methods: Mortality surveys

 –  Carcass searches

 –  Searcher efficiency trials

 –  Scavenger removal trials

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Factors included in fatality estimates

• # of carcasses found

• Searcher efficiency rate

Carcass removal rate by scavengers• Proportion of turbines searched

• Correction factor for non-searchable areas in

turbine search plots• Search interval (e.g., daily, weekly)

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Studies included in fatality summary(J. Costa, 2011. Post-construction wildlife monitoring and results at terrestrial wind

farms. Wind Energy and Wildlife Forum, Orono, ME, 5 May 2011)

• Maine –  Mars Hill (2007, 2008)

 –  Stetson Mountain I (2009)

 –  Stetson Mountain II (2010)

•New Hampshire –  Lempster (2009)

• New York –  Bliss (2008)

 –  Clinton (2008)

Cohocton and Dutch Hill (2009, 2010) –  Ellenburg (2008)

 –  Maple Ridge (2006, 2007, 2008)

 –  Munnsville (2008)

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Uncorrected proportions of bird and bat fatalities at

New England and New York

Wind Energy Facilities

Birds

Bats

(J. Costa, 2011. Post-construction wildlife monitoring and results at terrestrial wind farms.

Wind Energy and Wildlife Forum, Orono, ME, 5 May 2011)

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Passerine

Unidentified

GameRaptor

Shorebird

Waterfowl

Owl

Seabird

Uncorrected bird fatalities reported from

New York and New England wind energy facilities

(J. Costa, 2011. Post-construction wildlife monitoring and results at terrestrial wind farms.

Wind Energy and Wildlife Forum, Orono, ME, 5 May 2011)

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Golden-crowned Kinglet

Red-eyed Vireo

Magnolia Warbler

European Starling

Ruffed Grouse

Black-throated Blue

Warbler

Predominant bird fatalities at wind energy facilities

in New England and New York

(J. Costa, 2011. Post-construction wildlife monitoring and results at terrestrial wind farms.

Wind Energy and Wildlife Forum, Orono, ME, 5 May 2011)

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(J. Costa, 2011. Post-construction wildlife monitoring and results at terrestrial wind farms.

Wind Energy and Wildlife Forum, Orono, ME, 5 May 2011)

Uncorrected bat fatalities reported from

New York and New England wind energy facilities

Hoary bat

Little brown bat

Silver-haired bat

Eastern red bat

Big brown bat

Northern long-eared

bat

Tri-colored bat

Unidentified

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Min

Max

0

2

4

6

8

10

12

New

England (4)New York (6)

Mid-Atlantic

and

Southeast

(3)

Midwest (3) Southwest

and West (9) Northwest

(9)

Min

Max

(J. Costa, 2011. Post-construction wildlife monitoring and results at terrestrial wind farms.

Wind Energy and Wildlife Forum, Orono, ME, 5 May 2011)

Regional comparison of estimated

minimum and maximum bird mortalities(individual per turbine per study period)

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(J. Costa, 2011. Post-construction wildlife monitoring and results at terrestrial wind farms.

Wind Energy and Wildlife Forum, Orono, ME, 5 May 2011)

Regional comparison of estimated

minimum and maximum bat mortalities(individual per turbine per study period)

Min

Max

0

10

20

30

40

50

60

70

New EnglandNew York

Mid-Atlantic

and

Southeast

MidwestSouthwest

and West Northwest

Min

Max

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Indirect Impacts

• Impact types: Habitat loss, fragmentation, anddegradation

• Mechanisms: Forest clearing, human activity,

turbine noise• Affected organisms: Forest-dependent species

• Documentation methods: Before-after-

control-impact studies

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Indirect Impacts

• Indirect impacts in northeastern forests have

received little study to date

• Studies of impacts on American marten and

Bicknell’s thrush are currently underway at the

Granite Reliable Power project in Coos County, New

Hampshire

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• Standardization of methods and metrics is

needed to enable regional analyses of

mortality data

• Collaborative studies involving multiple sites

will be critically important in understanding

indirect impacts on wildlife

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Habitat Loss

• Habitats of greatest concern

 –  High elevation spruce-fir forest

• Limited supply on the landscape

• Support a number of habitat specialists

• Loss of area can lead to local extirpations if remaining

patch size is insufficient to support breeding population

 –  Ridge-top mast stands

• Provide important resource for wide-ranging species

• Loss of area can impact populations over large areas

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Habitat Degradation

• Habitats of greatest concern

 –  High elevation spruce-fir forest

• Cleared patches expose adjacent forest to increased

winds, which leads to progressive wind-throw onshallow soils

• Cleared patches expose adjacent forest floor to dryingeffects of sun and wind, decreasing invertebratepopulations that support insectivorous species

 –  Headwater streams and seeps• Roadcuts interrupt natural hydrology, create run-off

and siltation that degrade water quality

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Noise Impacts

• Essentially nothing is known about wildliferesponse to turbine noise in eastern forests

• Areas for research include

 –  Potential impacts on predator-prey relationships• Target species for study – owls

 –  Potential impacts on intra-species communication

• Target species for study – songbirds

 –  Potential impacts on large mammal winteringconcentrations

• Target species for study – moose and deer