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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.
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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