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    A Research Update on the Effects of

    Marcellus Shale exploration and developmenton wildlife habitat and birdsPRELIMINARY RESULTS

    Margaret Brittingham

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    Number of permits andwells drilled is increasing

    exponentially

    0

    1000

    2000

    3000

    4000

    5000

    6000

    7000

    2005 2006 2007 2008 2009 2010 2011

    Year

    N

    umberwells

    Permits

    Wells Drilled

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    Research Objectives

    Use a GIS analysis to quantifylandscape elements and forest cover

    pre and post Marcellus Determine local effects of well pads

    on songbird populations

    Determine landscape effects ofMarcellus development on birds

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    Our study is focused in a 11 county region in theNorthcentral part of the state where foresthabitat is most abundant

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    We focused on foresthabitat in the NC regionof the state because ofthe overlap between theMarcellus formation andcore forest habitat and

    the importance of thiscore forest to wildlife

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    Diversity of mammals is highest withinthe NC region of Core forest

    Joly and Myers 2001

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    Pennsylvania is a keystone state for many

    forest interior and area sensitive species

    Scarlet tanager 19% of Popin PA

    Wood thrush 9% of pop

    in PA

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    Hunting, Ecotourism,Aesthetics, Recreationare important in this

    region of the state> $5.5 Billion annually

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    Gas well development changes the landscape

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    Areas are cleared for the well pad

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    Completed padstabilized withstone

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    Locally, seismic testing, roads andpipelines create linear corridors

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    We conducted a GIS analysis using availablepermit/drilled data, before and after photos,

    ground truthing, and on the groundmeasurements to describe landscape change.Collaborators: Joe Bishop, Patrick Drohan,

    Kevin Yoder

    3147 wells 11% on public land, 89%private land

    2017 pads 6% on public land, 94 %private land

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    Mean well pad size is 4.9 acres

    n= 29 well pads NC PA

    X= 2.0 + 0.2 ha(4.9 acres)

    Range 0.6 6.4

    ha(1.5-15.5 acres)

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    6-74-52-31

    35

    30

    25

    20

    15

    10

    5

    0

    Number of Well per Pad

    PercentofWellPads

    Number of wells per pad

    (n=26)

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    Based on ~February 1, 2011 PADEP data,

    wells drilled to date.

    Prior land use where well was drilled

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    5262 total acres

    HabitatConversion

    from 1190Marcelluspads in NC

    region

    Forest

    PastureRow Crops

    Developed

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    Breeding bird atlas blocks were used as oursampling unit - Approximately 3.1 X 3.1 miles (6,400acres,2590 ha)

    Used in first and second PA BBA project

    Habitat data tied to animal abundance and distribution

    W l l t d f t ti i d f bl k

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    We calculated a fragmentation index for blocksin study area (Brooks et al.2009). Scoreranges from 0 (highly fragmented) to 1 (low or

    no fragmentation) Index includes:

    % Forest

    % core forest Mean patch size Impervious surfaces

    Land development index Road density For our blocks, correlation between

    Fragmentation index and % forest 0.92

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    2nd PA Breeding Bird Atlas Wilson and Brauning

    275 blocks in studyarea ranked in top 5or 10 % for state

    Mean Fragmentationscores = 0.85+0.006

    Range 0.59-1.00

    75% >0.78

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    Fragmentation index with well pads added

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    Change in number of BBA blocks byfragmentation index

    Category Pre-Marcellus

    PostMarcellus2011

    % Change

    Dark Green0.856-1.00

    219 201 8%

    Light +Dark Green0.768-1.0

    403 388 4%

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    For select blocks wemapped the entire

    infrastructure

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    Local Effects of Well Pads on BirdAbundance and Distribution

    14 well pad sites in 6 counties

    11 private land, 3 public land

    122 points surveyed twice Birds surveyed for 6 min within 50 m of

    point

    66 points within 50 m of pad

    56 points 150-250 m from pad

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    57 species recorded. 15 Speciesgreater than 15 observations

    Compared distribution near versusfar from pad

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    Category AwayNear

    30

    25

    20

    15

    10

    5

    0

    Num

    berofObservations

    Expected

    Observed

    Black-throated Blue Warbler

    Ten species were significantly more abundantaway from well pads than near well pads

    2 =24.52,

    p< 0.001

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    Category AwayNear

    20

    15

    10

    5

    0

    NumberofObserva

    tions

    Expected

    Observed

    Blue-headed Vireo

    Category AwayNear

    40

    30

    20

    10

    0

    NumberofObserv

    ations

    Expected

    Observed

    Ovenbird

    2

    =16.72, p< 0.001

    2 =10.31,p = 0.001

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    One species was significantly more abundantnear well pads than away from well pads

    Category AwayNear

    14

    12

    10

    8

    6

    4

    2

    0

    Numb

    erofObservations

    Expected

    Observed

    American Robin

    2 =7.23 ,

    p=0.007

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    Ten Species were only found near wellpads and not away from well pads

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    Ten Species were only found away from wellpads and not near well pads

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    Determine landscape level effects ofMarcellus Development on Birds

    Survey BBA blocksand mini-blocks(1/9th block) withdifferent levels ofMarcellus activity

    Plan to compare bird

    communities amongblocks and pre andpost Marcellus

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    Well pad density by blocks andmini-blocks

    Blocks:

    Well pad density =0.00-0.57/km2

    Mini- blocks:Well pad density =0.00-1.1/km2

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    36 blocks and 24 mini-blocks surveyed

    368 point counts

    105 species, 3,400 individuals

    Most common red-eyed vireo (344)and ovenbird(342)

    Data analysis will occur this fall

    Wh t ff t ill i li h ildlif

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    What effects will pipelines have on wildlifecommunities? 60,000 new miles of pipeline are

    predicted

    Pi li

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    Pipe lines actas barriers

    to dispersalfor somespecies

    Spotted Salamander

    And asavenues

    for invasionfor others

    Bown-headed Cowbird

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    Others use them as pathways fortravel or hunting

    Raccon or opposum

    D di h th m d i li

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    Depending on how they are managed, pipelinesmay provide brood habitat or nesting habitat

    currently limiting some species or may function

    as ecological traps

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    PipelineAdjacentto Road

    Length(meters)

    Yes 14386

    No 5651

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    Length

    (meters)

    Area(meters2)

    Newroads

    3611 22533

    Roadswidened 4112 26870

    Nochange

    12313 94138

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    Roads vary in habitatquality

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    Traffic Changes Bradford County

    3101

    35653691 3947

    63046008

    5706

    6726

    0

    1000

    2000

    3000

    4000

    5000

    6000

    7000

    SR 14, Seg 0310South of Troy

    SR 6, Seg 0320West of Burlington

    SR 6, Seg 0420East of Burlington

    SR 6, Seg 0500West of SR 220 & Towanda

    Traffic 5-Year Average vs. 2010 Counts

    5-Year Total Traffic Average

    5-Year Truck Traffic

    2010 Total Traffic Average

    2010 Truck Traffic

    310

    1300

    247

    1460

    274

    1260

    277

    967

    Source: PennDOT Engineering District 3-0

    R ff d d i

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    Ruffed grouse are edge specieswith specialized habitatrequirements

    + Open areas for feeding,insects, brood habitat

    + Possible increase in earlysuccessional and edgehabitat

    -Increase in number ofmammalian predators

    -Increase in disturbance-Increase in roads

    Ruffed Grouse

    Effects of development on

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    Effects of development onturkeys will depends on localconditions and restoration

    activities+ Open areas for

    feeding, insects, seeds

    -Loss of thermal cover,destruction of springseeps, increase in

    number of mammalianpredators, increase indisturbance

    Wild Turkey

    D d pt bl nd ill

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    Deer are very adaptable and willbenefit from openings but not

    from traffic and higher huntingpressure

    + Open areas forfeeding

    -Increase inroads, higherhunting pressure

    White-tailed deer Identify and protect important habitat

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    Identify and protect important habitatfeatures prior to development

    Provide private landowners with

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    Provide private landowners withassistance at the site development

    stage and for pad and pipeline

    restoration

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    Protect critical core forest

    habitat

    Manage pipelines and corridors to create

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    Manage pipelines and corridors to createhabitat that is not an ecological trap

    Restore pads and minimize the amount

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    Restore pads and minimize the amountof time that pads are non-habitat.

    http://www.flickr.com/photos/neprwa/3597395241/in/photostream
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    Monitor the land andreport problems

    Participate in research

    and monitoringprograms developed todetermine howpopulations are

    responding to changes

    Form broad coalitions with natural resource

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    Form broad coalitions with natural resourcerelated individuals and organizations

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    Special thanks to Penn State collaboratorsJ. Bishop, P. Drohan and S. Pabian

    and to students working on this project E.Barton, N. Fronk, K. Yoder

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    We thank the following organizationsand programs for research support

    Marcellus Center for Outreach and Research(MCOR) Marcellus Research Seed GrantProgram

    Heinz Endowments

    PA DCNR Wild Resource ConservationProgram

    Pennsylvania Game Commission State WildlifeGrants Program