Ponderosa pine seedling height growth beneath partial overstories in the central Oregon Cascade...
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Ponderosa pine seedling height growth be-neath partial overstories in
the central Oregon Cascade RangeWoongsoon Jang1
Christopher R. Keyes1, David L.R. Affleck1, and Douglas A. Maguire2
1Department of Forest Management, College of Forestry and Con-servation, University of Montana 2Department of Forest Engineering, Resources & Management, Oregon State University
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Partial overstory retention
• Compromise between timber production and ecological objec-
tives
– Enhance structural complexity
– Increase species diversity
• Facilitating ponderosa pine seedling recruitment and survival
– Enhance seed availability
– Ameliorate environmental stressors
• For silviculturists
– Effect on growth rates of seedling?
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Negative effects on seedling growth
• Negative relationship between seedling growth and over-
story density, distance, etc.
• But, number of study is few:
– Because seedling growth prior to overstory removal was not
concerned
– Overstory retention level is constrained and retained temporary
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Objectives
• Understand overstory/understory relationships of two-
aged ponderosa pine stands arising from dispersed
variable-retention harvests
– How the growth of seedlings and saplings is influenced by
varying levels of overstory retention
– How the overstory/seedling growth relationship changes in
different environments
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Climate of study site
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec0
10
20
30
40
50
60
70
80
90
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
Precipitation
Max. Temp.
Min. Temp.
Tem
per
atu
re (
F)
Pre
cip
itat
ion
(in
.)
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Site description
Block Stand Tree ha-1 BA(m2 ha-1)
QMD(cm)
Ave. Ht.(m)
Ave. LCR(%)
Shrub Cov.(%)
WarmSprings
101102103105107
1216172033
9.27.87.33.46.8
99.078.774.246.451.0
41.739.036.519.624.4
5053545855
6272797940
PringleFalls
203204205206207208
12839
1031923380
22.510.817.324.313.918.1
47.459.346.340.272.853.7
26.031.725.523.134.229.8
664458545750
4877399
7354
Fort Rock301302304
182047
4.23.3
13.2
54.846.159.8
21.815.624.4
617262
382540
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Collected dataVariable Group Parameter Unit Scale
Response Variable Seedling height growth (1994-99) cm individual
Potential Productivity
Seedling height at 1994 cm individual
Site index m plot
Planted treatment - plot
Site preparation - plot
Block - stand
Overstory Retention
Quadratic Mean Diameter cm plot
Tree density trees ha-1 plot
Stand Density Index - plot
Basal Area ft2 ac-1 plot
Understory Condition
Vegetation Coverage % plot
Overhead shrub presence - individual
Nearest Shrub Height cm individual
Distance to Nearest Shrub cm individual
Graminoid coverage % plot
Seedling density trees ha-1 plot
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Data analyses
• Generalized linear model (GLM)
– Random component (probability distribution)
• Gamma distribution
– Linear predictor
•
– Link function
• Log transformation
•
X
)ln( X )exp( X
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Results
Variable Group Parameter Est. Coeff. S.E. p-value
(Intercept) -0.2792 0.1953 0.1532
Potential Productivity
Seedling Ht (1994) 0.6464 0.0364 <0.0001
Site index 0.0490 0.004 <0.0001
Planted treatment 0.3228 0.0419 <0.0001
Site preparation -0.2825 0.0541 <0.0001
Block (PF) 1.1249 0.18270 <0.0001
Block (WS) 0.7492 0.1741 <0.0001
Ht×(PF) -0.2341 0.0426 <0.0001
Ht×(WS) -0.0333 0.0408 0.4151
Overstory RetentionQMD (15 m) -0.0009 0.0005 0.0565
Tree density (15m) -0.0055 0.0005 <0.0001
Understory condition Nearest Shrub Height 0.0018 0.0003 <0.0001
INGY 2012 Winter Tech Meeting
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Overstory vs. Understory
• Negative effect on seedling height growth
– 10 cm increase of QMD 0.92% reduction
• e-0.0092 = 0.9908
– Additional 10 tree/ha 5.35% reduction
• e-0.0550 = 0.9465
• Similar results with other studies and species
– Ponderosa pine (Oliver and Dolph,1992; McDonald and Abbott
1994)
– Douglas-fir (Isaac 1956; Wampler 1993; Hansen et al. 1995)
– Scots pine (Elfving and Jakobsson 2006)
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Best measure of overstory?
• Basal Area (BA)
– Many study have used
• E.g. Rose and Muir 1997; Acker et al. 1998; Page et al. 2001
– Not merely a measure of aboveground competition
– Correlated with foliage or canopy coverage, root com-
petition, etc.
• Combination of tree density and QMD
– Account for more variance than BA
INGY 2012 Winter Tech Meeting
AFMP University of Montana
How big should the plot size be?
• Key question from competition indices
– So-called “zone of influence” (Opie 1968)
• Optimum radius of overstory plot
– Vary with tree size (Wagner and Radosevich 1991)
– 3.5 times of the mean crown radius (Lorimer 1983)
• Bigger plot explains more variance
– Beyond 18.29 m ignorable (Hoyer 1993)
– Min. effective distance 12.19 m (McDonald 1976)
– Thus, 15 m radius is the most relevant
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Shade? Or others?
• What causes the reduction of seedling growth?
– Light condition
• Influences ponderosa pine seedlings more than any other factor
• Decreases with overstory basal area increment (Oliver and Dolph
1992)
• Modifies tree attributes (Pearson 1936, Messier et al. 1999)
– Others?
• Soil moisture (McDonald and Abbot 1994)
• Competition for nutrients and low soil temperature (Lajzerowicz et al.
2004)
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Prescribed burning
• Reduces fuel load, improves seedling recruitment, simulates
thinning effect, etc.
• However, the effect of prescribed burning has been debated
for a long time
• Negative effect in this study
– Loss of total biomass of duff layer
– Subsequent nutrient deficiency
• Takes long time to recover to the level of pre-burn
• Limitation of total nutrient supply (especially N)
• Delayed recovery of N-fixation shrubs
(eg. Ceanothus velutinus, Purshia tridentata)
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AFMP University of Montana
Planting
• Already selected seedlings
– Have better geno- & phenotype
• Already grown enough to compete
• Planter could control the place to be
planted
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AFMP University of Montana
Understory veg. & seedling growth
FR PF WS
05
01
00
15
02
00
25
03
00
Block
He
igh
t of N
ea
rest
Sh
rub
(cm
)
0 100 200 300 400
Height at 1994 (cm)
He
igh
t Gro
wth
Warm Springs
Fort Rock
Pringle Falls
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Management implications
• Controlling seedling height growth
– Manipulation of overstory retention level
• Number and size of overstory retention trees
• Introduction of site preparation method or artificial planting
• Effects of other factors on seedling behavior
– stand history, potential productivity, and understory condition
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Management implications
0 20 40 60 80 100 120 140
02
04
06
08
01
00
12
01
40
Number of trees per ha
QM
D (
cm)
0 -1 -2 -3 -4 -5 -6 -7 -8 -9 -10 -11 -12 -13 -14 -15 -16 -17
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Going further…
• Spatial pattern of overstory retention?
– Palik et al. 2003; Maguire et al. 2006
• Climate?
– How do seedlings respond to the weather during growing season?
• Refinement of understory veg. variables
– Plot level measurement were not appropriate
– Shrub species composition
– Interaction (e.g. competition vs. facilitation?) with seedling along
with site condition and seedling size, etc.
INGY 2012 Winter Tech Meeting
AFMP University of Montana
Cited literature• Acker, S.A., E. Zenner, and W. Emmingham. 1998. Structure and yield of two-aged stands on the Willamette National Forest, Oregon: implications for green tree reten-
tion. Canadian Journal of Forest Research 28(5):749-758.
• Hansen, A.J., S.L. Garman, J.F. Weigand, D.L. Urban, W.C. McComb, and M.G. Raphael. 1995. Alternative Silvicultural Regimes in the Pacific Northwest: Simulations of
Ecological and Economic Effects. Ecological Applications 5(3):535-554.
• Hoyer, G.E. 1993. The influence of Douglas-fir overstory on understory tree height growth in coastal forests of Washington. Washington Department Natural Resources
Forest Land Management Research Center. Contribution No. 348.
• Isaac, L.A. 1956. Place of partial cutting in old-growth stands of the Douglas-fir region. US Dept. of Agriculture, Forest Service, Pacific Northwest Forest and Range
Experiment Station. Research Paper 16. PNW-RP-16. p 48.
• Lajzerowicz, C.C., M.B. Walters, M. Krasowski, and H.B. Massicotte. 2004. Light and temperature differentially colimit subalpine fir and Engelmann spruce seedling
growth in partial-cut subalpine forests. Canadian Journal of Forest Research 34(1):249-260.
• Lorimer, C.G. 1983. Tests of age-independent competition indices for individual trees in natural hardwood stands. Forest Ecology and Management 6(4):343-360.
• Maguire, D., D. Mainwaring, and C. Halpern. 2006. Stand dynamics after variable-retention harvesting in mature Douglas-fir forests of western North America. Allge-
meine Forst und Jagdzeitung 177(6/7):120.
• McDonald, P.M. 1976. Inhibiting Effect of Ponderosa Pine Seed Trees on Seedling Growth. Journal of Forestry 74(4):220-224.
• McDonald, P.M., and C.S. Abbott. 1994. Seedfall, regeneration, and seedling development in group-selection openings. U.S. Department of Agriculture, Forest Service
Research Paper PSW-RP-220. 13p.
• Messier, C., R. Doucet, J.-C. Ruel, Y. Claveau, C. Kelly, and M.J. Lechowicz. 1999. Functional ecology of advance regeneration in relation to light in boreal forests. Cana-
dian Journal of Forest Research 29(6):812-823.
• Oliver, W.W., and L.K. Dolph. 1992. Mixed-conifer seedling growth varies in response to overstory release. Forest Ecology and Management 48(1-2):179-183.
• Opie, J.E. 1968. Predictability of Individual Tree Growth Using Various Definitions of Competing Basal Area. Forest Science 14(3):314-323.
• Page, L.M., A.D. Cameron, and G.C. Clarke. 2001. Influence of overstorey basal area on density and growth of advance regeneration of Sitka spruce in variably thinned
stands. Forest Ecology and Management 151(1-3):25-35.
• Palik, B., R.J. Mitchell, S. Pecot, M. Battaglia, and M. Pu. 2003. Spatial distribution of overstory retention influences resources and growth of longleaf pine seedlings.
Ecological Applications 13(3):674-686.
• Pearson, G.A. 1936. Some Observations on the Reaction of Pine Seedlings to Shade. Ecology 17(2):270-276.
• Rose, C.R., and P.S. Muir. 1997. Green-tree retention: consequences for timber production in forests of the western Cascades, Oregon. Ecological Applications
7(1):209-217.
• Wagner, R.G., and S.R. Radosevich. 1991. Neighborhood predictors of interspecific competition in young Douglas-fir plantations. Canadian Journal of Forest Research
21(6):821-828.
• Wampler, M. 1993. Growth of Douglas-fir Under Partial Overstory Retention. M.S. thesis, University of Washington, Seattle, WA.