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Habitat requirements of Boreal Owl (Aegolius funereus) and Pygmy Owl (Glaucidium passerinum) in mountainous populations on the Balkan Peninsula
Boris Nikolov, Stoyan Stoyanov, Thomas Groen,
Iva Hristova-Nikolova, Tzvetan Zlatanov
24.07.2015 2
Advanced multifunctional forest management in European mountain ranges 2
Study area
•
Map of Bulgaria with georeferenced image of high resolution satellite imagery of
the study area from Google- Earth.
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Advanced multifunctional forest management in European mountain ranges 3
Shiroka Laka Forest Enterprise in “Trigrad-Mursalitsa” Natura-2000 zone
according to the Birds Directive
Study area
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Advanced multifunctional forest management in European mountain ranges 4
Shiroka Laka Forest Enterprise in “Trigrad-Mursalitsa” Natura-2000 zone
according to the Birds Directive
Study area
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Advanced multifunctional forest management in European mountain ranges 5
Study area
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Studied species
Two species of boreal owls:
• glacial relics
• high conservation value (Appendix I
of the Birds Directive)
Boreal Owl
(Aegolius
funereus) Pygmy Owl
(Glaucidium passerinum)
www.birdphoto.fi
www.birdphoto.fi
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Two species of boreal owls:
• Widely distributed in the taiga zone of Eurasia (both species) and
North America (Boreal Owl);
• Balkan Peninsula holds relic mountain populations (isolated refugia?)
– little is known about their habitat requirements.
Studied species
Boreal Owl
(Aegolius funereus)
Pygmy Owl
(Glaucidium passerinum)
www.owlpages.com
www.owlpages.com
http://www.owlpages.com/http://www.owlpages.com/
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Advanced multifunctional forest management in European mountain ranges 8
Data collection – birds
Field work performed in autumn 2012
• A total of 49.9km transects surveyed, all above 1450m altitude
• 85 point counts performed (34 points successful, which is 40%)
Target owl species recorded:
• Boreal Owl (Aegolius funereus) - 29 birds in 27 territories
• Pygmy Owl (Glaucidium passerinum) - 10 birds in 9 territories
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Data collection – birds
Territories of:
• Boreal Owls
• Pygmy Owls
• Both species
Localities
ascertained
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Data collection – stand parameters
Field work performed in 2013 and 2014
• 85 “complexes of plots” established (85 point counts performed)
• 25 plots in each complex or a total of 2125 plots
• Predominantly spruce dominated forests, very few plots dominated
by Scots pine
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360 m
30 m
Data collection – stand parameters
Total area sampled ~ 13 ha
Sampling intensity ~ 2%
100 m2 x 25
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360 m
30 m
Data collection – stand parameters
Total area sampled ~ 13 ha
Sampling intensity ~ 2%
100 m2 x 25
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Advanced multifunctional forest management in European mountain ranges 13
Predictor variables
Growing stock [m3/ha)
Fellings ≤ 3 years old (% plots)
Fellings 4-10 years old (% plots)
Fellings ≥ 4 years old (% plots)
Canopy closure ≤ 0.3 (% plots)
Canopy closure 0.6-0.8 (% plots)
Mean canopy closure
DBH ≥ 38 / ha (# trees)
DBH ≥ 38 (% plots)
DBH ≥ 42 / ha (# trees)
DBH ≥ 42 (% plots)
DBH ≥ 50 / ha (# trees)
DBH ≥ 50 (% plots)
DBH ≥ 58 / ha (# trees)
DBH ≥ 58 (% plots)
Fallen dead wood (m3/ha)
Standing dead wood (m3/ha)
Fallen dead wood Decay stage 1 (m3/ha)
Fallen dead wood Decay stage 2 (m3/ha)
Fallen dead wood Decay stage 3 (m3/ha)
Fallen dead wood Decay stage 4 (m3/ha)
Fallen dead wood Decay stage 5 (m3/ha)
Standing dead wood Decay stage 1 (m3/ha)
Standing dead wood Decay stage 2 (m3/ha)
Standing dead wood Decay stage 3 (m3/ha)
Standing dead wood Decay stage 4 (m3/ha)
Standing dead wood Decay stage 5 (m3/ha)
Many predictor variables correlated!
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Explanatory variables - Boreal Owl
Growing stock [m3/ha) – α≤0.05
Fellings ≤ 3 years old (% plots)
Fellings 4-10 years old (% plots)
Fellings ≥ 4 years old (% plots)
Canopy closure ≤ 0.3 (% plots)
Canopy closure 0.6-0.8 (% plots)
Mean canopy closure
DBH ≥ 38 / ha (# trees)
DBH ≥ 38 (% plots)
DBH ≥ 42 / ha (# trees)
DBH ≥ 42 (% plots)
DBH ≥ 50 / ha (# trees)
DBH ≥ 50 (% plots)
DBH ≥ 58 / ha (# trees)
DBH ≥ 58 (% plots)
Fallen dead wood total (m3/ha) – 0.05≤α≤0.1
Standing dead wood total (m3/ha)
Fallen dead wood Decay stage 1 (m3/ha)
Fallen dead wood Decay stage 2 (m3/ha)
Fallen dead wood Decay stage 3 (m3/ha)
Fallen dead wood Decay stage 4 (m3/ha)
Fallen dead wood Decay stage 5 (m3/ha)
Fallen dead wood Decay stage 4&5 (m3/ha)
Standing dead wood Decay stage 1 (m3/ha)
Standing dead wood Decay stage 2 (m3/ha)
Standing dead wood Decay stage 3 (m3/ha)
Standing dead wood Decay stage 4 (m3/ha)
Standing dead wood Decay stage 5 (m3/ha)
Standing dead wood Decay stage 4&5 (m3/ha)
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Explanatory variables - Pygmy Owl
Growing stock [m3/ha)
Fellings ≤ 3 years old (% plots)
Fellings 4-10 years old (% plots)
Fellings ≥ 4 years old (% plots)
Canopy closure ≤ 0.3 (% plots)
Canopy closure 0.6-0.8 (% plots)
Mean canopy closure
DBH ≥ 38 / ha (# trees)
DBH ≥ 38 (% plots)
DBH ≥ 42 / ha (# trees)
DBH ≥ 42 (% plots)
DBH ≥ 50 / ha (# trees)
DBH ≥ 50 (% plots)
DBH ≥ 58 / ha (# trees)
DBH ≥ 58 (% plots)
Fallen dead wood (m3/ha)
Standing dead wood (m3/ha)
Fallen dead wood Decay stage 1 (m3/ha)
Fallen dead wood Decay stage 2 (m3/ha)
Fallen dead wood Decay stage 3 (m3/ha)
Fallen dead wood Decay stage 4 (m3/ha)
Fallen dead wood Decay stage 5 (m3/ha)
Fallen dead wood Decay stage 4&5 (m3/ha)
Standing dead wood Decay stage 1 (m3/ha)
Standing dead wood Decay stage 2 (m3/ha)
Standing dead wood Decay stage 3 (m3/ha)
Standing dead wood Decay stage 4 (m3/ha)
Standing dead wood Decay stage 5 (m3/ha)
Standing dead wood Decay stage 4&5 (m3/ha)
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•
Modelling
Glaucidium
observations
Stand
parameters
Aegolius
observations
Collinearity
Analysis, PCA
logistic
regression
model (GLM)
Model performance:
• Area under the ROC curve
(ROC) statistic;•
• Kappa statistic &
• True skill statistics (TSS)
Principle of parsimony for
finding the minimal
adequate model (AIC)
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Modelling - the final set of variables
The final set of selected variables after
the collinearity analysis (PCA)
• Fellings 4-10 years old (% plots)
• Canopy closure ≤ 0.3 (% plots)
• DBH ≥ 50 (% plots)
• Fallen dead wood (m3/ha)
• Fallen dead wood Decay stage 4
(m3/ha)
• Standing dead wood Decay stage 4&5
(m3/ha)
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Best model (GLM) - Boreal Owl
The best parsimonious model for the Boreal owl (Aegolius funereus)
included three explanatory variables
The minimal adequate model for Boreal owl, R2 = 0.29 (Nagelkerke), P <
0.01, AIC = 87.26, * p < 0.05, ** p < 0.01, *** p < 0.001.
Included B(SE)
95 % CI for odds ratio
Lower Odds ratio Upper
Constant -0.940 (0.583)
Canopy closure ≤ 0.3 (% plots) -0.042 (0.018)** 0.922 0.959 0.990
DBH ≥ 50 (% plots) 0.038 (0.020)* 1.000 1.039 1.083
Fallen dead wood Decay stage 4
(m3/ha)
0.175 (0.071) ** 1.040 1.191 1.387
There are no issues related to the basic residual statistics for the model
(leverage, studentized residuals and DFBeta values)
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Best model (GLM) - Boreal Owl
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• Area under the ROC curve (ROC) statistic – 0.7 – reasonable accuracies
ROC value ranges between 0.5 and 1, where 0.5 means a discrimination which is
no different than random, and a value of 1 means perfect discrimination of
presence and absence.
• Kappa statistic – 0.4
The Kappa statistic ranges between 0 and 1 and indicates the accuracy, corrected
for the random chance of correctly assigning presences and absences.
• True skill statistics (TSS) – 0.4
A TSS of 1 indicates perfect discrimination of presences and absences, and a TSS
of -1 indicates an inverse result (i.e. absences are perfectly assigned as presence
and vice versa).
Best model (GLM) - Boreal Owl
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Advanced multifunctional forest management in European mountain ranges 21
Best model (GLM) - Pygmy Owl
Included B(SE) 95 % CI for odds ratio
Lower Odds ratio Upper
Constant -3.812 (0.0815)***
Fallen dead wood
(m3/ha)
0.087 (0.032)** 1.029 1.090 1.168
The best parsimonious model for the Pigmy owl (Glaucidium
passerinum) included only one explanatory variable – rooting logs.
The minimal adequate model for Pigmy owl, R2 = 0.213
(Nagelkerke), P < 0.01, AIC = 47.419, * p < 0.05, ** p < 0.01,
*** p < 0.001.
There are no issues related to the basic residual
statistics for the model (leverage, studentized
residuals and DFBeta values)
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Advanced multifunctional forest management in European mountain ranges 22
• Area under the ROC curve (ROC) statistic – 0.55 – high randomness
ROC value ranges between 0.5 and 1, where 0.5 means a discrimination which is
no different than random, and a value of 1 means perfect discrimination of
presence and absence.
• Kappa statistic – 0.4
The Kappa statistic ranges between 0 and 1 and indicates the accuracy, corrected
for the random chance of correctly assigning presences and absences.
• True skill statistics (TSS) – 0.2
A TSS of 1 indicates perfect discrimination of presences and absences, and a TSS
of -1 indicates an inverse result (i.e. absences are perfectly assigned as presence
and vice versa).
Best model (GLM) - Pygmy Owl
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Model robustness
Glaucidium - Accuracies
Ave
rag
e a
ccu
racy (
+/-
sd
)
GLM CTA SRE FDA MARS RF
0.0
0.2
0.4
0.6
0.8
1.0
ROCTSSKAPPA
Aegolius - Accuracies
Ave
rag
e a
ccu
racy (
+/-
sd
)
GLM CTA SRE FDA MARS RF
0.0
0.2
0.4
0.6
ROCTSSKAPPA
Biomod modelling
• Generalized Linear Models (GLM)
• Random Forest (RF)
• Surface Range Envelope (SRE)
• Classification Tree Analysis (CTA)
• Multiple Adaptive regression
splines (MARS)
• Flexible Discriminant Analysis
(FDA)
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Model robustness
Possible reasons for the relatively high randomness in the models
(between 20 and 30% of the variance explained)
• Sampling bias, only “suitable areas” included in visited locations,
therefore no “unsuitable” locations in dataset for contrast to show
importance of variables.
• Very few successful observations of Pygmy owl – the species is too
rare.
• Missed variables to consider (i.e. presence of Tawny Owl – Strix
aluco)
• Low sampling intensity ~ 2%
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Model robustness
Total area sampled ~ 13 ha
Sampling intensity ~ 2%
Areas not well represented
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Model robustness
Smaller than expected
nesting territory ~ 50 ha?
Total area sampled ~ 13 ha
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Thresholds
FDWDecay stage 4
0 1 2
m3/h
a
0
2
4
6
8
10
12
14
DBH 50 cm or more
0 1 2
# tre
es/h
a
0
20
40
60
80
100
DBH 50 cm or more
0 1 2
% p
lots
0
10
20
30
40
50
60
Canopy closure
of 0.3 or less
0 1 2
% p
lots
0
10
20
30
40
50
60
Boreal Owl
FDW total
0 1 2
m3/h
a
0
10
20
30
40
50
Only plots where Boreal Owl is present are shown in the figures
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Thresholds
Canopy closure0.3 or more
0 1 2
% p
lots
0
20
40
60
80
100
DBH 50cm or more
0 1 2
% p
lots
0
10
20
30
40
50
FDW total
0 1 2
m3/h
a
10
15
20
25
30
35
40
45
DBH 50cm and more
0 1 2
#tr
ee
s/h
a
0
10
20
30
40
50
60
70
80
Pigmy Owl
FDWDecade stage 4
0 1 2
m3
/ha
0
5
10
15
20
25
30
Only plots where Pigmy Owl is present are shown in the figures
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Management implications
Both species moderately tolerant to management
(less so Pigmy owl)
Continuous cover forestry
Elements of oldgrowthness on some 10% of the territory
24.07.2015Advanced multifunctional forest management in European mountain ranges
Thank you for your attention!