dan gibson erik blomberg michael atamian jim sedinger

21
A multi-scale approach to assess sage-grouse nesting habitat Comparing nest site selection and nest success Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Upload: katen

Post on 14-Jan-2016

56 views

Category:

Documents


0 download

DESCRIPTION

A multi-scale approach to assess sage-grouse nesting habitat Comparing nest site selection and nest success. Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger. Overview: Sage-grouse. Why is knowledge regarding habitat use important?. - PowerPoint PPT Presentation

TRANSCRIPT

Page 1: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

A multi-scale approach to assess sage-grouse nesting habitat

Comparing nest site selection and nest success

Dan GibsonErik BlombergMichael AtamianJim Sedinger

Page 2: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Overview: Sage-grouse

Page 3: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

• Habitat degradation is the primary mechanism driving sage-grouse population declines

• Habitat will continue to be degraded

• We need to establish what habitat is important (during various life history stages) for species persistence at multiple scales and manage it appropriately

Why is knowledge regarding habitat use important?

Page 4: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

So, what is “important” habitat?

• Is it being used?

• Are individuals successful?

• In theory, the relationship between habitat selection and success compares what habitat features improved fitness along an organism’s evolved life history, and what improves fitness in its current environment

Page 5: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Research Objectives

• Investigate which habitat characteristics sage-grouse are being selecting for as nesting habitat and how they influence nest success

• Use this information to develop tools to make more informed management decisions

Page 6: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

• Monitored female sage-grouse from 2003-2012 in Eureka Co. Nevada

• Ground level vegetation data was collected at nest and random sites

• ~410 nests

Page 7: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Analyses• Nest Site Selection (RSF models)

– Binomial generalized linear mixed models (GLMM) in R (lme4 package)

• Random effects: year and individual

– Two independent analyses performed (two scales: “spatial” and “local”

• Nest Survival– Nest survival module in Program

MARK• Predictor variables

– Ground-scale vegetation– Spatial-scale habitat structure– Temporal – Disturbance – Individual heterogeneity

Page 8: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Results • Nest Survival

– Estimates of overall nest survival were low (17%)• Note: It is very difficult to achieve a lambda >1.0 at this level of

success

• Selection• Local: selection pressures were the greatest for various forms of

cover and forb availability• Spatial: provided a mechanism to delineate nesting from available

habitat using relatively coarse spatial metrics

• Very few habitat features were supported to influence both nest selection and nest success

Page 9: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Covariate Beta Survival SE Beta Selection SESeason -0.21 0.06 N/A N/AClutch Size 0.21 0.06 N/A N/ANon-Sagebrush Shrub Cover 0.30 0.09 0.69 0.19 2

Forb Cover 0.25 0.08 0.42 0.19 2

Interaction 0.32 0.12 -0.10 0.28 2

Wildfire 2000m -0.12 0.07 0.41 0.23 1

Wildfire 2000m2 -0.04 0.04 -0.14 0.10 1

Pinyon-Juniper 2000m 0.12 0.11 0.41 0.23 1

Pinyon-Juniper 2000m2-0.02 0.04 -0.27 0.14 1

Distance from lek 0.07 0.07 -0.64 0.09 1

Habitat classified as sagebrush within 1000m 0.01 0.09 1.43 0.12 1

Interaction 0.01 0.06 -0.62 0.08 1

Slope -0.05 0.09 0.51 0.10 1

Elevation 0.09 0.09 0.60 0.08 1

Interaction -0.05 0.07 -0.33 0.07 1

Shrub Height 0.12 0.06 -0.46 0.19 2

Forb Richness 0.05 0.06 0.25 0.12 2

Average Forb Height 0.05 0.07 0.21 0.12 2

Residual Grass Height 0.03 0.07 0.38 0.14 2

Grass Cover -0.02 0.07 0.37 0.14 2

Interaction -0.05 0.06 0.34 0.14 2

Non-Sagebrush Shrub Cover 0.28 0.11 1.00 0.22 2

Non-Sagebrush Shrub Cover2 -0.02 0.03 -0.10 0.05 2

Sagebrush Shrub Cover 0.10 0.07 0.98 0.15 2

Sagebrush Shrub Cover2-0.02 0.04 -0.13 0.08 2

1 denotes spatial selection model

2 denotes local selection model

Bold values significant

Selection versus Survival

Page 10: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Proportion non-sagebrush shrub cover

0.0 0.2 0.4 0.6 0.8 1.0

Re

lati

ve p

rob

ab

ilit

y o

f u

se

0.0

0.2

0.4

0.6

0.8

1.0

Relative Probability of SelectionNestsAvailable

0.0

0.2

0.4

0.6

0.8

1.0

0

10

20

3040

5060

70

0.00.2

0.40.6

0.8

Ove

rall

pro

bab

ilit

y o

f n

est

su

rviv

al (

un

til

37

day

s)

Perc

ent f

orb

cove

r

Proportion non-sagebrush shrub cover

Successful NestsFailed Nests

Non-sagebrush shrub cover & Forb cover

Percent Forb Cover

0 10 20 30 40 50 60

Rel

ati

ve p

rob

abil

ity

of

use

0.0

0.2

0.4

0.6

0.8

1.0

Relative Probability of SelectionNestsAvailable

Page 11: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Sagebrush canopy cover

Proportion sagebrush shrub cover

0.0 0.2 0.4 0.6 0.8 1.0

Pro

bab

ilit

y o

f n

est

site

sel

ecti

on

or

nes

t su

cces

s

0.0

0.2

0.4

0.6

0.8

1.0

Relative Probability of UseOverall Probability of Nest SuccessNests

* Guidelines to manage sage grouse populations and their habitats Connelly et al. 2000

Page 12: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Grass cover * Residual grass height

0.5

0.6

0.7

0.8

0.9

1.0

0

20

40

60

80

020

4060

Rel

ativ

e p

rob

abili

ty o

f u

se

Perc

ent G

rass

Cov

erResidual Grass Height (cm)

Available Used

0.0

0.1

0.2

0.3

0.4

0

20

40

60

80

020

4060O

vera

ll p

rob

abili

ty o

f n

est

surv

ival

Perc

ent g

rass

cov

er

Residual grass height (cm)

Nests0.0 0.1 0.2 0.3

Page 13: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

* Guidelines to manage sage grouse populations and their habitats Connelly et al. 2000

Page 14: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Proportion of habitat classified as Pinyon-Juniper

0.0 0.2 0.4 0.6 0.8

Pro

babi

lity

of u

se/s

ucce

ss

0.0

0.2

0.4

0.6

0.8

1.0

Weighted probability of useProbability of nest survival (until 37 days)

Pinyon-Juniper encroachment

Page 15: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Proportion of habitat converted to exotic grasslands due to wildfire

0.0 0.2 0.4 0.6 0.8

Pro

babi

lity

of u

se/n

est s

urvi

val

0.0

0.2

0.4

0.6

0.8

1.0

Weighted probability of useProbability of nest survival (until 37 days)

Exotic Grasslands

Page 16: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

• Very few habitat features exhibited a selective pressure and influenced nest success

• Current management decisions geared to improve sage-grouse populations through modifying nesting conditions may ultimately not be successful

• Current guidelines for management of sage-grouse nesting habitat do not appear to be appropriate for central Nevada

• So, can we develop tools to assist management?

Summary so far…

Page 17: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Elevation * Slope + Distance from lek * Amount of habitat classified as sagebrush (1000m)

Developing a nesting habitat use model

0.0

0.2

0.4

0.6

0.8

1.0

0

5

10

1520

2530

35

16001800

20002200

24002600

28003000

Rel

ativ

e P

rob

abili

ty o

f U

se

Slop

e (d

egre

es)

Elevation (m)

Nests

0.0

0.2

0.4

0.6

0.8

1.0

0

20

40

60

80

100

02000

40006000

800010000

1200014000

Rel

ativ

e P

rob

abili

ty o

f U

se

Perc

ent o

f Sur

roun

ding

Hab

itat

Cla

ssifi

ed a

s Sa

gebr

ush

Distance from Lek (m)

Nests

Page 18: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Delineation of nesting habitat

• ~18% of surrounding habitat was classified as suitable which encompassed 75% of nest points

• Estimate of concordance = 0.72

Page 19: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

• Independently collected nest locations fit the model well … for the most part

• Additionally, statewide spring telemetry locations fell within “suitable habitat” at a high rate

Suitability Threshold

0.0 0.2 0.4 0.6 0.8 1.0

Pro

po

rtio

n o

f ne

sts

cla

ssifi

ed

to b

e in

su

itab

le h

ab

itat

0.0

0.2

0.4

0.6

0.8

1.0 Central/Northeast NevadaEureka CountyNorthwest NevadaVirginia Mountains

Page 20: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

Demographiccontinuity NestingEarly Brood RearingLate Brood Rearing

*Atamian et al. 2010

• Establish what habitats are required during “important” life history stages

• Protect the commonalities

• Allow for connectivity between stages

Probability of Use

Page 21: Dan Gibson Erik Blomberg Michael Atamian Jim Sedinger

• Thanks to: – Jim Sedinger, Erik Blomberg, and

Mike Atamian

– Shawn Espinosa, Chet Van Dellan (NDOW) and Peter Coates (USGS)

– All previous graduate students, technicians, and volunteers that have worked on this project

– All funding sources: