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Population-level implications for climate change for a montane forest songbird Sarah J K Frey   Allan M Strong   Kent P McFarland AOU 2009 Philadelphia
Mountains & Climate Change
Focal Species: Bicknell’s Thrush ,[object Object]
Vulnerable to climate change
Available data,[object Object]
Fewer & smaller patches = HABITAT LOSS (Rodenhouse et al. 2008 Mitig Adapt Strateg Glob Change) Remaining habitat will likely change in quality (Beckage et al. 2008 PNAS) alteration of successional processes Predictions – Hypotheses
If this is happening, then BITH populations will have to respond in one of 3 ways Predictions – Hypotheses
Change their behavior (adapt to the new conditions) Predictions – Hypotheses
2. Move to a new location (latitude or elevation) Predictions – Hypotheses
3. Decline/go extinct Predictions – Hypotheses
Multi-season Occupancy Model (MacKenzie et al. 2003 Ecology) Population Parameters Occupancy		 Colonization Detection		 Extinction Methods - Model Between seasons Colonization or extinction 1,2,3 1,2,3 1,2,3 1,2,3 Surveys Seasons    1  			   2				 3				4 Occupancy & detection Within seasons
Habitat Covariates Local = boreal basal area (BBA) (Beckage et al. 2008 PNAS) Landscape = patch size (Lambert et al. 2005 Wilson Bull) Methods - Model
Climcalc(http://www.pnet.sr.unh.edu/climcalc/)  Mean July Temp (MJT) calculated - lat, long, elv, slp, asp Current MJT envelope for BITH habitat Methods – Landscape Climate Data
Landscape:  + 1° C to MJT envelope Local (BBA): MJT inc. over time (amnt. of time for 1° C inc. = 7 yrs.) Northeast Climate Data (www.northeastclimatedata.org)	 A1 Scenario  Methods – Warming Predictions
Current & future (+1°C) maps of predicted habitat amount (landscape) & suitability (patch) Compared amount and quality of habitat  Estimated occupancy, colonization, and extinction now and with 1°C of warming Methods – Population Predictions
Occupancy (Boreal Basal Area * Patch Size) Colonization (Boreal Basal Area) Extinction (Boreal Basal Area + Patch Size) Detection (Survey + Patch Size) Methods - Model
No time lag – once pixel moves out of MJT envelope, it is no longer available as habitat Boreal basal area is a good indicator of local habitat quality Beckage et al. 2008 model realistically represents changes in the composition of local habitat over time Lambert et al. 2005 model is a realistic representation of current potential habitat availability at the landscape scale Model Assumptions
Results - Landscape # of patches decreased from 128 to 29 Total amount of habitat reduced by 67%
Results - Landscape # of patches decreased from 128 to 29 Total amount of habitat reduced by 67%
Results - Local Avg. patch size increased 44.6% (90.5 to 130.8 ha) Remaining patches = higher quality BBA 29.1 - 60.6 m2/ha Total BBA decreased 31.3%
Results - Local Avg. patch size increased 44.6% (90.5 to 130.8 ha) Remaining patches = higher quality BBA 29.1 - 60.6 m2/ha Total BBA/patch decreased 31.3%
Results - Population parameters occupancy colonization
Results - Occupancy Current
Results - Occupancy +1OC
Results - Colonization Current
Results - Colonization +1OC
Colonization least influenced by changes in landscape scale features, although total area available for colonization decreased by 66.8% Results - Population parameters
Results - Extinction Current
Results - Extinction +1OC
Population implications are primarily related to the total amount of habitat lost Composition of montane patches altered – less so than overall amount of habitat Loss of lower elevation sites likely has less of an impact - represent marginal habitat (?) Conclusions
Under small amounts of warming, Bicknell’s Thrush may be able to persist in the remaining high quality patches > 1°C of warming may call into question the long term persistence of this species in Vermont  Conclusions
Landscape - Increased Warming
Landscape - Increased Warming
Landscape - Increased Warming
Hope for Bicknell’s ?
70+ year dataset on Mt. Washington (NH) shows that warming at high elevations may be occurring at a slower rate than at lower elevations (Seidel et al. 2009 Arctic, Antarctic, and Alpine Research) Hope for Bicknell’s?

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Climate Change Threatens Montane Forest Songbird

  • 1. Population-level implications for climate change for a montane forest songbird Sarah J K Frey Allan M Strong Kent P McFarland AOU 2009 Philadelphia
  • 3.
  • 5.
  • 6. Fewer & smaller patches = HABITAT LOSS (Rodenhouse et al. 2008 Mitig Adapt Strateg Glob Change) Remaining habitat will likely change in quality (Beckage et al. 2008 PNAS) alteration of successional processes Predictions – Hypotheses
  • 7. If this is happening, then BITH populations will have to respond in one of 3 ways Predictions – Hypotheses
  • 8. Change their behavior (adapt to the new conditions) Predictions – Hypotheses
  • 9. 2. Move to a new location (latitude or elevation) Predictions – Hypotheses
  • 10. 3. Decline/go extinct Predictions – Hypotheses
  • 11. Multi-season Occupancy Model (MacKenzie et al. 2003 Ecology) Population Parameters Occupancy  Colonization Detection  Extinction Methods - Model Between seasons Colonization or extinction 1,2,3 1,2,3 1,2,3 1,2,3 Surveys Seasons 1 2 3 4 Occupancy & detection Within seasons
  • 12. Habitat Covariates Local = boreal basal area (BBA) (Beckage et al. 2008 PNAS) Landscape = patch size (Lambert et al. 2005 Wilson Bull) Methods - Model
  • 13. Climcalc(http://www.pnet.sr.unh.edu/climcalc/) Mean July Temp (MJT) calculated - lat, long, elv, slp, asp Current MJT envelope for BITH habitat Methods – Landscape Climate Data
  • 14. Landscape: + 1° C to MJT envelope Local (BBA): MJT inc. over time (amnt. of time for 1° C inc. = 7 yrs.) Northeast Climate Data (www.northeastclimatedata.org) A1 Scenario Methods – Warming Predictions
  • 15. Current & future (+1°C) maps of predicted habitat amount (landscape) & suitability (patch) Compared amount and quality of habitat Estimated occupancy, colonization, and extinction now and with 1°C of warming Methods – Population Predictions
  • 16. Occupancy (Boreal Basal Area * Patch Size) Colonization (Boreal Basal Area) Extinction (Boreal Basal Area + Patch Size) Detection (Survey + Patch Size) Methods - Model
  • 17. No time lag – once pixel moves out of MJT envelope, it is no longer available as habitat Boreal basal area is a good indicator of local habitat quality Beckage et al. 2008 model realistically represents changes in the composition of local habitat over time Lambert et al. 2005 model is a realistic representation of current potential habitat availability at the landscape scale Model Assumptions
  • 18. Results - Landscape # of patches decreased from 128 to 29 Total amount of habitat reduced by 67%
  • 19. Results - Landscape # of patches decreased from 128 to 29 Total amount of habitat reduced by 67%
  • 20. Results - Local Avg. patch size increased 44.6% (90.5 to 130.8 ha) Remaining patches = higher quality BBA 29.1 - 60.6 m2/ha Total BBA decreased 31.3%
  • 21. Results - Local Avg. patch size increased 44.6% (90.5 to 130.8 ha) Remaining patches = higher quality BBA 29.1 - 60.6 m2/ha Total BBA/patch decreased 31.3%
  • 22. Results - Population parameters occupancy colonization
  • 27. Colonization least influenced by changes in landscape scale features, although total area available for colonization decreased by 66.8% Results - Population parameters
  • 30. Population implications are primarily related to the total amount of habitat lost Composition of montane patches altered – less so than overall amount of habitat Loss of lower elevation sites likely has less of an impact - represent marginal habitat (?) Conclusions
  • 31. Under small amounts of warming, Bicknell’s Thrush may be able to persist in the remaining high quality patches > 1°C of warming may call into question the long term persistence of this species in Vermont Conclusions
  • 36. 70+ year dataset on Mt. Washington (NH) shows that warming at high elevations may be occurring at a slower rate than at lower elevations (Seidel et al. 2009 Arctic, Antarctic, and Alpine Research) Hope for Bicknell’s?
  • 37.

Editor's Notes

  1. Montane systems in the NE are relatively uncommon and their existence depends on cooler climates at high elevations, making them particularly vulnerable to climate change.
  2. Since BITH is a high-elevation specialist, moving up in elevation is not a long-term viable solution
  3. Uses detection/non-detection data to estimate the following parameters. 88 sites across VT were surveyed 1-3 times in 2006 & 2007
  4. Boreal basal area measured at 88 sites across VT. Patch size calculated from the BITH potential habitat model .Ran 65 models => every combination of local and landscape for each parameter (single, additive, interaction). Patch size calculated from potential habitat model (potential habitat identified by presence-absence of BITH, cutoff by elevation which changes by latitude, and then pixels of coniferous dominated forest (landcover map)
  5. Raster of MJT for current BITH distribution
  6. AICc weight =0.16. Top 6 models within 2 AICc points of top model all very similar. Used as input variables for the metapopulation model to estimate the following parameters currently and with one degree of warming
  7. Graph of the % change in the avg. parameter value between current & predicted conditions
  8. Further explanation 3rd bullet = there are smaller proportions of habitat conditions favored by this high elevation disturbance specialist