Abstract
• Context
A century and more after a major reforestation program, large areas in the French Southern Alps have moved to a landscape mosaic of old pine plantations and new, heterogeneous and uneven-aged, mixed stands. These conditions are challenging foresters in silvicultural practices and management choices.
• Aims
The aims of this study are to understand, analyze, model, and simulate the ongoing phenomena, and to propose a decision-making tool.
• Methods
An individual-based forest dynamics model considering recruitment, growth, and mortality (as related to the spatial arrangement of stands and species, to site conditions and competition) and a simulation system including spatial sampling are designed and calibrated to allow simulation of both silviculture treatments at the stand level and management strategies at the forest or landscape level.
• Results
By keeping track of the trees while simulating at the forest level, they offer an alternative to upscaling strategies and a suitable tool for prediction of stand and forest characteristics in situations influenced by strong driving forces such as colonization and forest maturation.
• Conclusion
This approach is a straightforward means for adjusting forest management to trends such as expansion of shade-tolerant species; as spatial and temporal variation in site conditions are accounted for, it is also a promising way towards predicting their warming-induced upward shift.
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Acknowledgments
First of all, I would like to express my gratitude to the research technicians involved in establishing plots and in data collection, especially to Maurice Turrel and Nicolas Mariotte as reliable and essential forest technicians. I also thank the non-permanent staff and the students who participated in measuring the experiments. I am particularly grateful to the French National Forest Service (ONF) involved since the initiation of this program, to its head in Avignon, its local officers on the mount Ventoux, and its research unit (namely to Jean Ladier), for help in finding suitable survey sites and for information about forest stands and site conditions. I am also greatly indebted to the French National Forest Inventory (IFN), namely to Nabila Hamza and Éric Bruno, for providing a large dataset and explanations about the methods of IFN. Special thanks go to François de Coligny (INRA-AMAP), always available for assistance in programming on Capsis platform. Thanks also to INRA URFM administrative staff for assistance in management of the financial support mentioned hereafter. Finally, many thanks to three reviewers who provided constructive comments and suggestions on earlier versions of the manuscript.
Funding
This study was partly supported by ECOFOR (www.gip-ecofor.org) and by the French Ministry in charge of Ecology and Sustainable Development.
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Appendix: Parameter estimates and regression statistics for each submodel and species
Appendix: Parameter estimates and regression statistics for each submodel and species
Hereafter, “R 2” denotes the coefficient of determination, “mean” is the mean of dependent variable, “CVR” is the residual coefficient of variation (standard deviation of the residuals divided by the mean of the dependent variable), in percent, and “N” is the sample size.
Recruitment submodel (see also Fig. 1)
Abies alba
(R 2 = 0.67, mean = 0.55/year, CVR = 105%, N = 59)
Parameter | Value | Standard error |
r1 | −0.51 | 0.56 |
r2 | 11.65 | 3.69 |
r3 | 0.40 | 0.15 |
Pinus nigra
(R 2 = 0.13, mean = 0.39/year, CVR = 155%, N = 179)
Parameter | Value | Standard error |
r1 | −0.046 | 0.129 |
r2 | 5 | fixed |
r3 | 0.75 | 0.09 |
Pinus sylvestris
(R 2 = 0.06, mean = 0.17/year, CVR = 137%, N = 214)
Parameter | Value | Standard error |
r1 | 0.10 | 0.06 |
r2 | 1.04 | 2.13 |
r3 | 0.70 | 0.84 |
Pinus uncinata
(R 2 = 0.05, mean = 0.21/year, CVR = 162%, N = 188)
Parameter | Value | Standard error |
r1 | 0.10 | fixed |
r2 | 1.02 | 0.88 |
r3 | 0.56 | 0.28 |
Fagus sylvatica
(R 2 = 0.27, mean = 1.02/year, CVR = 90%, N = 214)
Parameter | Value | Standard error |
r1 | 4.17 | 4.28 |
r2 | 0.30 | 0.63 |
r3 | 0.34 | 0.29 |
Diameter Growth submodel for Trees
Pinus nigra, P. sylvestris, P. uncinata
(R 2 = 0.88, mean = 0.36 cm/year, CVR = 22%, N = 654)
Parameter | Value | Standard error |
a1 | −45.98 | 11.68 |
a2 | 64.10 | 12.46 |
a3 | 0.0212 | 0.0093 |
a4 | 0.401 | 0.060 |
a5 | 19.72 | 6.42 |
a6 | 1.23 | 0.13 |
a7 | 0.232 | 0.054 |
a8 | 0.015 | 0.0033 |
Equation 2a was fitted only for P. nigra. As P. sylvestris and P. uncinata have many traits in common with P. nigra, we used a correspondence (set up using D2; not presented) between diameter increment of each three species, as depending on HdomINC5, NBA, and ICS.
Abies alba
N.B. : In this case, ICS is computed using dbh under bark, and DINC5 is the increment under bark. The switch between under bark and over bark dbh values is achieved using bark thickness relationships (established using D2, not presented). NBA is over bark.
(R 2 = 0.61, mean = 0.38 cm/year, CVR = 32%, N = 644)
Parameter | Value | Standard error |
b1 | 0.122 | 0.061 |
b2 | 4.09 | 2.56 |
b3 | 0.151 | 0.053 |
b4 | 0.786 | 0.052 |
b5 | 0.014 | 0.007 |
b6 | 3.55 | 0.55 |
Fagus sylvatica
N.B.: underbark and overbark values: see Eq. 2b
(R 2 = 0.69, mean = 0.25 cm/year, CVR = 29%, N = 686)
Parameter | Value | Standard error |
c1 | 1.28 | 0.18 |
c2 | 0.1 | fixed |
c3 | 0.86 | 0.05 |
c4 | 0.056 | 0.053 |
c5 | 0.020 | 0.002 |
c6 | 0.84 | 0.07 |
Diameter Growth submodel Seedlings and saplings
When parameter d4 is non-significant (“NS”), the modifier \( {e^{{ - \left( {d4 - {{H} \left/ {{H\max }} \right.}} \right)}}}^2 \)is not included (i.e. it is replaced by 1).
Abies alba
(R 2 = 0.83, mean = 0.27 cm/year, CVR = 40%, N = 864)
Parameter | Value | Standard error |
d1 | 12.99 | 0.80 |
d2 | 0.1 | fixed |
d3 | 1.24 | 0.19 |
d4 | - | NS |
d5 | −0.071 | 0.024 |
d6 | 0.72 | 0.08 |
d7 | 2.08 | 0.15 |
d8 | 1.38 | 0.16 |
d9 | 2 | fixed |
N.B.: d5 < 0 : i.e. SDLp is favorable to diameter growth of Abies alba seedlings/saplings.
Fagus sylvatica
(R 2 = 0.51, mean = 0.25 cm/year, CVR = 47%, N = 1,065)
Parameter | Value | Standard error |
d1 | 6.34 | 0.58 |
d2 | 0.25 | 0.07 |
d3 | 5.01 | 1.10 |
d4 | - | NS |
d5 | 0.048 | 0.029 |
d6 | 0.51 | 0.067 |
d7 | 1.59 | 0.20 |
d8 | 0.46 | 0.12 |
d9 | 2 | fixed |
Pinus nigra
(R 2 = 0.45, mean = 0.46 cm/year, CVR = 35%, N = 448)
Parameter | Value | Standard error |
d1 | 8.57 | 0.62 |
d2 | −0.056 | 0.333 |
d3 | 14.28 | 4.97 |
d4 | 0.19 | 0.05 |
d5 | 0.40 | 0.07 |
d6 | 1.47 | 0.53 |
d7 | 1.65 | 0.44 |
d8 | 13.59 | 6.65 |
d9 | 8 | fixed |
D3 contains too few growth samples or site/stand conditions for Pinus sylvestris or P. uncinata; for simulation, we used the relationship fitted for Pinus nigra.
Height–Diameter submodel for Trees
With \( s = s0 + s1 \cdot {\rm Re} lSpcgMod \) (see § 2.4.4)
Abies alba
(R 2 = 0.97, mean = 17.34 m, CVR = 12%, N = 5,689)
Parameter | Value | Standard error |
s1 | 0.000257 | 0.000024 |
s0 | 0.0130 | 0.00214 |
Fagus sylvatica
(R 2 = 0.92, mean = 12.55 m, CVR = 14%, N = 16,081)
s1 | 0.000535 | 0.000016 |
s0 | 0.0300 | 0.00161 |
Pinus nigra
(R 2 = 0.97, mean = 12.54 m, CVR = 11%, N = 9,846)
s1 | 0.000131 | 0.000015 |
s0 | 0.0659 | 0.00175 |
Pinus sylvestris
(R 2 = 0.94, mean = 10.28 m, CVR = 14%, N = 24,397)
s1 | 0.000342 | 9.175E-6 |
s0 | 0.0276 | 0.00129 |
Pinus uncinata
(R 2 = 0.93, mean = 9.76 m, CVR = 15%, N = 3,696)
s1 | 0.000089 | 0.000021 |
s0 | 0.0505 | 0.00304 |
Height Growth submodel for Seedlings and saplings (see also Fig. 2)
When parameter t3 is non-significant (“NS”), the term \( {\text{ ((1 - H / Hmax)}}{{ }^{\text{t3}}}{ } + { 0}{.01)} \) is not included (i.e. it is replaced by 1).
Abies alba
(R 2 = 0.67, mean = 0.38 m/m, CVR = 65%, N = 1,173)
Parameter | Value | Standard error |
t1 | 34.1 | 3.5 |
t2 | 8 | fixed |
t3 | - | NS |
t4 | 0.29 | 0.06 |
t5 | 2.18 | 0.30 |
t6 | 0.12 | 0.05 |
t7 | 0.50 | 0.39 |
Fagus sylvatica
(R 2 = 0.30, mean = 0.75 m/m, CVR = 56%, N = 1,161)
Parameter | Value | Standard error |
t1 | 6.98 | 1.39 |
t2 | 2 | fixed |
t3 | 5.32 | 1.23 |
t4 | 0.15 | 0.05 |
t5 | 1.67 | 0.35 |
t6 | 0.009 | 0.053 |
t7 | 2 | fixed |
Pinus nigra, Pinus sylvestris and P. uncinata
(R 2 = 0.65, mean = 0.62 m/m, CVR = 33%, N = 760)
Parameter | Value | Standard error |
t1 | 6.69 | 1.11 |
t2 | 2.43 | 0.30 |
t3 | 14.81 | 1.57 |
t4 | 1.39 | 0.46 |
t5 | 2.39 | 0.53 |
t6 | 5.06 | 2.56 |
t7 | 10.48 | 2.80 |
For Pinus sylvestris or P. uncinata, D3 contains too few individuals with height growth measurements and the corresponding range of site/stand conditions is quite narrow; for simulation, we used the relationship fitted for P. nigra.
Mortality submodels
Trees
DBH and Ddom are under bark values. N is the number of combinations of classes of NBA (8 classes ranging between 10 and 60 m2/ha) by classes of DBH/Ddom (7 ranging between 0.3 and 1.1). The mean is the mortality rate for 5 years.
Abies alba
(R 2 = 0.32, mean = 0.0186, CVR = 93%, N = 48)
Parameter | Value | Standard error |
m1 | −0.0088 | 0.035 |
m2 | 0.0022 | 0.0012 |
m3 | −2.09 | 1.25 |
m4 | 0.0021 | 0.0178 |
Fagus sylvatica
(R 2 = 0.40, mean = 0.0037, CVR = 72%, N = 56)
m1 | −0.0014 | 0.0016 |
m2 | 0.00026 | 0.00008 |
m3 | −0.33 | 0.70 |
m4 | −0.011 | 0.015 |
Pinus nigra
(R 2 = 0.55, mean = 0.0060, CVR = 65%, N = 49)
m1 | 0.0028 | 0.0089 |
m2 | 0.00086 | 0.00033 |
m3 | −2.48 | 1.08 |
m4 | −0.0012 | 0.0257 |
Pinus sylvestris
(R 2 = 0.76, mean = 0.0186, CVR = 22%, N = 42)
m1 | 0.0066 | 0.0064 |
m2 | 0.0013 | 0.0003 |
m3 | −0.48 | 0.32 |
m4 | −0.028 | 0.009 |
Pinus uncinata
(R 2 = 0.14, mean = 0.0195, CVR = 54%, N = 53)
m1 | 0.00051 | 0.00523 |
m2 | 0.00082 | 0.00026 |
m3 | 0.92 | 0.53 |
m4 | −0.037 | 0.014 |
Seedlings/Saplings (see also Fig. 3)
N is the number of combinations of classes of NBA (from 10 to 60 with classes of width 10 m2/ha) by classes of H/Hmax (from 0.1 to 1.0 with classes of width 0.1). The mean is the mortality rate for 5 years.
Abies alba
(R 2 = 0.85, mean = 0. 0175, CVR = 115%, N = 27)
Parameter | Value | Standard error |
m0 | 2.803E-7 | 8.569E-8 |
Fagus sylvatica
(R 2 = 0.30, mean = 0.0095, CVR = 210%, N = 29)
m0 | 4.607E-7 | 1.147E-7 |
Pinus nigra
(R 2 = 0.56, mean = 0. 0395, CVR = 122%, N = 25)
m0 | 1.408E-6 | 3.186E-7 |
Pinus sylvestris
(R 2 = 0.94, mean = 0. 0295, CVR = 51%, N = 11)
m0 | 1.007E-6 | 3.027E-7 |
Dataset D3 contains too few samples for Pinus uncinata; for simulation, we used the relationship fitted for Pinus nigra.
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Dreyfus, P. Joint simulation of stand dynamics and landscape evolution using a tree-level model for mixed uneven-aged forests. Annals of Forest Science 69, 283–303 (2012). https://doi.org/10.1007/s13595-011-0163-2
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DOI: https://doi.org/10.1007/s13595-011-0163-2