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Biodiversity across the forest cycle in ash and Sitka spruce plantations:
Stand structure and vegetation change
Laura French, George Smith, Saoirse O’Donoghue, Anne-Marie McKee, Sue Iremonger, Daniel Kelly,
Fraser Mitchell
Department of Botany, Trinity College Dublin
Forestry and biodiversity
• Forestry an increasing land use in Ireland
• Can represent a threat to existing biodiversity
Forestry and biodiversity
• Forestry an increasing land use in Ireland
• Can represent a threat to existing biodiversity
• Can be an opportunity to enhance biodiversity at local and landscape scales
Objectives
• How does stand structure develop in plantations?
• How does species richness change over the forest cycle?
Objectives
• How does stand structure develop in plantations?
• How does species richness change over the forest cycle?
• How does tree species influence vegetation species richness?
Objectives
• How does stand structure develop in plantations?
• How does species richness change over the forest cycle?
• How does tree species influence vegetation species richness?
• How does species richness of typical woodland plants change?
Study sites
• 20 Sitka spruce• 12 ash• 12 spruce-ash mix
• Spruce 5 - 46 yr old• Ash 5 - 80 yr old
• 3 100m2 plots per site / species combination
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Sitka spruce
ash
Sitka spruce structural typesPCA Ordination
Axis 1 (Var Expl = 73%)
Axi
s 2
(Var
Exp
l = 2
1%)
Prethicket
30% Canopy Cover
Sitka spruce structural typesPCA Ordination
Axis 1 (Var Expl = 73%)
Axi
s 2
(Var
Exp
l = 2
1%)
Thicket
80% Canopy Cover
Sitka spruce structural typesPCA Ordination
Axis 1 (Var Expl = 73%)
Axi
s 2
(Var
Exp
l = 2
1%)
Closed-maturing
87% Canopy Cover
Sitka spruce structural typesPCA Ordination
Axis 1 (Var Expl = 73%)
Axi
s 2
(Var
Exp
l = 2
1%)
Reopening
71% Canopy Cover
Sitka spruce structural typesPCA Ordination
Axis 1 (Var Expl = 73%)
Axi
s 2
(Var
Exp
l = 2
1%)
Mature
55% Canopy Cover
Species richness over the Sitka spruce forest cycle
Me
an
sp
eci
es
ric
hn
es
s
pe
r plo
t
Vascular plants Bryophytes
0
5
10
15
20
25
Pre Thk Clo Reo Mat
A
B
C
BC
A
0
5
10
15
20
25
Pre Thk Clo Reo Mat
A
BCC
BCB
Canopy cover and species richness
y = -0.6162x + 63.062
R2 = 0.71
0
5
10
15
20
25
30
35
40
45
30 50 70 90
Canopy cover (% cover per 100 m2 quadrat)
Me
an
to
tal s
pe
cie
s
ric
hn
es
s p
er
plo
t
Species richness over the ash forest cycle
0
5
10
15
20
25
Pre Pol Clo Semi MatMe
an
sp
eci
es
ric
hn
es
s
pe
r plo
t
Vascular plants Bryophytes
A A
BBB
0
5
10
15
20
25
Pre Pol Clo Semi Mat
A
ABB B
AB
Ash compared with Sitka spruce
Me
an
sp
eci
es
ric
hn
es
s
pe
r plo
t
Ash Sitka spruce
0
5
10
15
20
25
30
Vascular Plants Bryophytes Total
A
B
A
A A
B
Woodland species over the forest cycle
0
2
4
6
8
10
Pre Thk Clo Reo MatMe
an
sp
eci
es
ric
hn
es
s
pe
r plo
t
Ash Sitka spruce
AAB
C
B
A
0
2
4
6
8
10
Pre Pol Clo Semi Mat
A AB
CD
D
BC
Conclusions
• Species richness changes significantly over the forest cycle
• Ash forests have higher species richness of vascular plants
Conclusions
• Species richness changes significantly over the forest cycle
• Ash forests have higher species richness of vascular plants
• Sitka spruce forests have higher species richness of bryophytes
Conclusions
• Species richness changes significantly over the forest cycle
• Ash forests have higher species richness of vascular plants
• Sitka spruce forests have higher species richness of bryophytes
• Species richness of woodland vascular plants increases along forest cycle
Conclusions
• Plantations of ash and Sitka spruce are not necessarily “ecological deserts”
• Not “oases of biodiversity” either