Text S1. Statistical estimation of parameters in submodels

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Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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Text S1: Statistical estimation of parameters in submodels
The following section presents additional details on parameterization of the submodels
for the individual-based model (IBM). All parameters were were estimated using Markov Chain
Monte Carlo simulations in JAGS v. 4.3.0 [1], with four chains, each run for 110,000 iterations
with a burn-in of 10000 iterations. To reduce autocorrelation, we retained every 200th iteration
from each chain. Convergence was assessed using the Gelman-Rubin diagnostic with a
threshold of 1.1 [2], and by visually examining output from the chains. We assigned noninformative priors to most parameters, with parameters of these non-informative priors
constrained to biologically reasonable values (Table S1). Parameter estimates are shown in
Table S2. In this supplementary text, we provide details on statistical estimation of parameters in
submodels; for further details on data collection of seeds, seedlings and fruit production see [3].
For further details on data collection of trees >1 cm DBH in the 50 ha Forest Dynamics Plot, see
[4,5].
Fruit production
The fruit production model estimates fruit production as a function of tree size using data
on fallen fruit (including peels of fruit dispersed by frugivores) measured directly beneath parent
trees in 3 m x 3 m fruit count quadrat h (42 total quadrats). Fruit production was modeled as a
π‘“π‘Ÿ
Poisson random variable with a mean (λβ„Ž ) modeled as a sigmoid function of tree size (DBH),
π‘“π‘Ÿ
π‘“π‘Ÿ
π‘“π‘Ÿ
with three free parameters (𝛽0 , 𝛽1 , 𝛽2 ).
π‘“π‘Ÿ
π‘“π‘Ÿπ‘’π‘–π‘‘π‘ β„Ž ~Poisson(λβ„Ž )
π‘“π‘Ÿ
λβ„Ž
=
π‘“π‘Ÿ
𝛽0
+
(1)
1
π‘“π‘Ÿ
π‘“π‘Ÿ
π‘“π‘Ÿ
𝛽1 +exp(𝛽2 ×DBHβ„Ž )
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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π‘“π‘Ÿ
In this equation, 𝛽0 represents baseline fruit production for a 20 cm DBH tree (the observed
π‘“π‘Ÿ
minimum size of reproductive trees), 𝛽1 represents limiting fruit production as DBH gets large,
π‘“π‘Ÿ
and 𝛽2 is the per unit increase in fruit production as DBH increases.
We assumed that total canopy area of any tree of reproductive size was equal to 89 m2 ,
the mean canopy area of reproductive Miliusa trees. Alternate models including canopy area as a
function of DBH did not improve model fit. Thus, total fecundity per tree g is equal to:
π‘“π‘Ÿπ‘’π‘–π‘‘π‘ β„Ž
𝑓𝑒𝑐𝑒𝑛𝑑𝑖𝑑𝑦𝑔 = (
) × 89 m2
Unit area
(2)
Seedling establishment
We modeled germination as a binomial random variable using data on 6500 seeds
experimentally added to 1 m x 1 m quadrat i in plot j, with the number of experimentally added
𝑒π‘₯𝑝
seeds equal to N𝑖,𝑗
. As with other submodels for tree growth and survival, we assumed that
π‘”π‘’π‘Ÿ
germination probability, θ𝑖,𝑗 , was a function of conspecific seedling density and tree
neighborhoods. We accounted for spatial non-independence in our data by including a normally
π‘”π‘’π‘Ÿ
distributed plot-level random effect, πœ€π‘—
. The model is formally described as follows for seed
addition quadrat i (281 total quadrats) in plot j (93 plots):
π‘”π‘’π‘Ÿ
𝑒π‘₯𝑝
Experimental new recruits ~Binomial(θ𝑖,𝑗 , N𝑖,𝑗
)
π‘”π‘’π‘Ÿ
π‘”π‘’π‘Ÿ
+ 𝛽 π‘”π‘’π‘Ÿ × Con. seedlings𝑖 +
DBH. neighbori
π‘”π‘’π‘Ÿ
𝛼 π‘”π‘’π‘Ÿ × ∑
+πœ€π‘—
𝑑𝑖𝑠.π‘”π‘’π‘Ÿ
Distance. neighbori
logit(θ𝑖
) = πœ‡0
(3)
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
π‘”π‘’π‘Ÿ
In this equation, πœ‡0
3
is baseline germination rate, 𝛽 π‘”π‘’π‘Ÿ is the linear decrease in seed survival as
seedling conspecific density increases, 𝛼 π‘”π‘’π‘Ÿ represents the magnitude of NDD from tree
neighborhoods, and 𝑑𝑖𝑠. π‘”π‘’π‘Ÿ represents the distance decay of NDD.
Seed dispersal
We estimated seed dispersal parameters by combining data on fruit production by
sampled reproductive adults, germination probability, and the spatial distribution of newly
germinated seedlings relative to adults. This approach enables us to directly estimate seed
dispersal kernels from the distributions of natural seedlings. New recruit abundance in quadrat i
(1723 quadrats) within plot j (219 plots) was modeled as a Binomial-distributed random variable
π‘”π‘’π‘Ÿ
with a a probability of success equal to the probability of germination (θ𝑖,𝑗 ) and a number of
π‘”π‘’π‘Ÿ
π‘›π‘Žπ‘‘
trials equal to natural seed arrival (N𝑖,𝑗
). θ𝑖,𝑗 is known from the seed addition experiment
π‘›π‘Žπ‘‘
𝑠𝑒𝑒𝑑𝑠
data, and N𝑖,𝑗
is estimated as a Poisson-distributed random variable with mean equal to λ𝑖,𝑗
:
π‘”π‘’π‘Ÿ
π‘›π‘Žπ‘‘
Natural new recruits𝑖,𝑗 ~Binomial(θ𝑖,𝑗 , N𝑖,𝑗
)
(4)
π‘›π‘Žπ‘‘
𝑠𝑒𝑒𝑑𝑠
N𝑖,𝑗
~ Poisson(λ𝑖,𝑗
)
(5)
𝑠𝑒𝑒𝑑𝑠
Expected seed arrival (λ𝑖,𝑗
) is the sum of seed rain from adult trees within a 20 m radius
around each new recruit quadrat (πΏπ‘œπ‘π‘Žπ‘™ 𝑠𝑒𝑒𝑑 π‘Ÿπ‘Žπ‘–π‘›π‘–,𝑗 ) and seed rain from sources outside of the
20 m radius, (π΅π‘Žπ‘‘β„Žπ‘–.𝑗 ):
𝑠𝑒𝑒𝑑𝑠
λ𝑖,𝑗
= (πΏπ‘œπ‘π‘Žπ‘™ 𝑠𝑒𝑒𝑑 π‘Ÿπ‘Žπ‘–π‘›π‘–,𝑗 + exp[π΅π‘Žπ‘‘β„Ž])
(6)
πΏπ‘œπ‘π‘Žπ‘™ 𝑠𝑒𝑒𝑑 π‘Ÿπ‘Žπ‘–π‘›π‘–,𝑗 = ∑𝑛𝑔=1 𝑓𝑒𝑐𝑒𝑛𝑑𝑖𝑑𝑦𝑔 × π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™π‘”
(7)
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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The Bath term is necessary in the model to represent seedling quadrats where seedlings were
counted but no trees were present in the local neighborhood. The Local seed rain term includes
the model for fecundity per tree g (𝑓𝑒𝑐𝑒𝑛𝑑𝑖𝑑𝑦𝑔,𝑖,𝑗 ; Eq. 3), summed over all trees in a 20 m radius
around quadrat k in plot j, and a dispersal submodel (π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™π‘” ). The dispersal submodel
represents the probability of seed arrival at a certain distance from tree g and was modeled as a
two-dimensional Student’s T distribution with three degrees of freedom, following [6,7].
π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™π‘”
1
=
[
2
2
distance𝑔
)
(πœ‹×exp[𝑒.π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™])(1+
exp[𝑒.π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™]
(8)
]
In the equation above, the parameter 𝑒. π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™ represents the shape of the dispersal kernel.
Initial height of seedlings
We parameterized a submodel for the initial height of seedlings using data on the initial
height of 628 seedlings from the seed addition experiment, with height measured three months
after seed addition. Initial height of the ith seedling in plot j was modeled as a skew normal
distribution:
𝑖𝑛.β„Žπ‘‘
Initial height 𝑖,𝑗 ~Skew Normal(μ𝑖𝑛.β„Žπ‘‘
, π‘ π‘π‘Žπ‘™π‘’ 𝑖𝑛.β„Žπ‘‘ )
𝑖,𝑗 , π‘ β„Žπ‘Žπ‘π‘’
(9)
We modeled the expectation, μπ‘–π‘›β„Žπ‘‘
𝑖,𝑗 , of initial seedling height as a constant term with a normally
distributed plot-level random effect, πœ€π‘—π‘–π‘›β„Žπ‘‘ , to represent non-independence of seedlings within the
same seed addition plot:
π‘–π‘›β„Žπ‘‘
μπ‘–π‘›β„Žπ‘‘
+ πœ€π‘—π‘–π‘›β„Žπ‘‘
𝑖,𝑗 = 𝛽0
(10)
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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Seedling survival and growth
To parameterize models for seedling survival and growth, we used annual censuses of
1505 seedlings in 174 plots. Seedling survival was modeled as a Bernoulli distribution and
seedling growth was modeled as a skew normal distribution. Both models included a normally
distributed random effect (πœ€π‘–,𝑗 ), a linear term for size-dependence, (Size𝑖 ), and a term for NDD
from conspecific seedling density (𝛽 𝑠𝑠 ). Unlike submodels for germination, seedling growth,
tree growth and tree survival, preliminary analysis revealed that the tree neighborhood term did
not improve model fit for seedling survival. Consequently, we did not include this term in the
submodel for seedling survival.
𝑠𝑠
Seedling survival 𝑖,𝑗 ~Bernoulli(θ𝑖,𝑗
)
𝑠𝑠
𝑠𝑠
logit(θ𝑖,𝑗
) = πœ‡0𝑠𝑠 + 𝑠𝑖𝑧𝑒 𝑠𝑠 × Size𝑖 + 𝛽 𝑠𝑠 × Con. seedlings𝑖 + πœ€π‘–,𝑗
(11)
𝑠𝑔
Seedling growth𝑖 ~Skew Normal(μ𝑖 , π‘ β„Žπ‘Žπ‘π‘’ 𝑠𝑔 , π‘ π‘π‘Žπ‘™π‘’ 𝑠𝑔 )
𝑠𝑔
𝑠𝑔
μ𝑖 = (πœ‡0 + 𝑠𝑖𝑧𝑒 𝑠𝑔 × Size𝑖 ) × exp(𝛽 𝑠𝑔 × Con. seedlings𝑖 )
𝛼𝑠𝑔
× exp (Size × ∑
𝑖
DBH.neighborj
Distance.neighborj 𝑑𝑖𝑠.𝑠𝑔
)+
(12)
𝑠𝑔
πœ€π‘–,𝑗
In the equation above, size represents the linear effect of size on probability of seedling survival
and seedling growth. Variance in the skew normal distribution is a function of two parameters, shape
and scale. Skewness (in this case a tendency towards positive growth) is a function of the shape
parameter. Parameters for NDD are described in Equation 3.
Seedling height-DBH allometry
Because seedling size was measured in height (cm) and tree size was measured in DBH
(cm), the IBM requires an expression to translate seedling height into diameter as seedlings grow
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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into saplings. We parameterized two equations for seedling height-DBH allometry using DBH
and height measurement data from 45 seedlings. The first allometric expression quantifies the
probability that a seedling of a certain height, Height 𝑖 , is >1 cm DBH:
π‘‡π‘Ÿπ‘’π‘’ π‘ π‘€π‘–π‘‘π‘β„Žπ‘– ~Bernoulli(θπ‘–π‘ π‘€π‘–π‘‘π‘β„Ž )
(13)
logit(θπ‘–π‘ π‘€π‘–π‘‘π‘β„Ž ) = π‘Ž π‘ π‘€π‘–π‘‘π‘β„Ž + 𝑏 π‘ π‘€π‘–π‘‘π‘β„Ž × Height 𝑖
The second allometric expression applies only to seedlings that have a Tree switch value of 1,
and predicts a DBH measurement for new trees as a normally-distributed random variable:
β„Žπ‘‘
Tree DBH𝑖 ~Normal(μβ„Žπ‘‘
𝑖 ,𝜎 )
(14)
μβ„Žπ‘‘
𝑖
=π‘Ž
β„Žπ‘‘
+𝑏
β„Žπ‘‘
× Height 𝑖
Tree survival and tree growth
We estimated tree survival and growth using 2,049 tagged individuals censused at five
year intervals from 1994 to 2004 in a 50 ha Forest Dynamics Plot. Survival was modeled as a
Bernoulli distribution and growth was modeled as a skew-normal distribution. The probability of
survival (θπ‘Žπ‘  ) and the expectation of growth (μπ‘Žπ‘” ) included terms for both size and In these
equations, DBH𝑖 represents the DBH of the ith individual, with DBH. neighbor𝑗 and
Distance. neighborj representing the size and distance of neighbor tree j in a 25 m radius around
the target individual. The first term in the models for tree survival and growth is the Hossfeld IV
function, a function of tree DBH [8]. The Hossfeld IV function includes two free parameters, G
and P. The second term is the function for NDD from tree neighborhood, including two free
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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parameters, 𝛼, which determines the strength of NDD, and 𝑑𝑖𝑠. π‘Žπ‘ , which determines the
distance decay of NDD over the tree neighborhood. Tree survival was modeled as a Bernoulli
distribution and tree growth was modeled as a skew normal distribution.
Tree survival ~Bernoulli(θπ‘Žπ‘ 
𝑖 )
logit(θπ‘Žπ‘ 
𝑖 )=
2×𝐺.𝑠×DBH𝑖
2
DBH𝑖 2
(𝐺.𝑠+
)
𝑃.𝑠
π›Όπ‘Žπ‘ 
+ DBH × ∑
𝑖
π‘Žπ‘”
DBH.neighbor𝑗
Distance.neighborj 𝑑𝑖𝑠.π‘Žπ‘ 
π‘Žπ‘”
(15)
π‘Žπ‘”
Tree growth𝑖 ~Skew Normal(μ𝑖 , π‘ β„Žπ‘Žπ‘π‘’π‘– , π‘ π‘π‘Žπ‘™π‘’π‘– )
π‘Žπ‘”
μ𝑖 =
π›Όπ‘Žπ‘”
2×𝐺.𝑔×DBH𝑖
(𝐺.𝑔+
DBH𝑖 2
)
𝑃.𝑔
×∑
2 × exp (
DBH
𝑖,𝑗
DBH.neighborj
Distance.neighborj
(16)
𝑑𝑖𝑠.π‘Žπ‘” )
Similar to population structure in other plants [9], our data revealed changing variance as
a function of tree size. Consequently, we modeled shape and scale of the skew normal
distribution for adult growth as functions of tree size (DBH):
π‘Žπ‘”
π‘ β„Žπ‘Žπ‘π‘’π‘–
= π‘π‘ β„Žπ‘Žπ‘π‘’ × exp( DBH𝑖 × π‘Žπ‘ β„Žπ‘Žπ‘π‘’ )
π‘Žπ‘”
π‘ π‘π‘Žπ‘™π‘’π‘–
(17)
= √π‘Žπ‘ π‘π‘Žπ‘™π‘’ × DBH𝑖 π‘π‘ π‘π‘Žπ‘™π‘’
References
1. Plummer, M. 2003 JAGS: A program for analysis of Bayesian graphical models using Gibbs
sampling. URL http://citeseer.ist.psu.edu/plummer03jags.html.
2. Gelman, A. & Rubin, D. B. 1992 Inference from iterative simulation using multiple
sequences. Stat. Sci. 7, 457–472.
3. Caughlin, T. T., Ferguson, J. M., Lichstein, J. W., Bunyavejchewin, S. & Levey, D. J. 2013
The importance of long-distance seed dispersal for the demography and distribution of a
canopy tree species. Ecology 95, 952–962. (doi:10.1890/13-0580.1)
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4. Bunyavejchewin, S., LaFrankie, J. V. & Ashton, P. S. 2000 Population Ecology of Trees in
Huai Kha Khaeng Wildlife Sanctuary, Thailand: Data from the 50-ha Forest Dynamics Plot.
Smithson. Trop. Res. Inst. Balboa Panama
5. Bunyavejchewin, S., Baker, P. J., LaFrankie, J. V. & Ashton, P. S. 2004 Huai Kha Khaeng
Forest Dynamics Plot, Thailand. Trop. For. Divers. Dynamism Find. Large-Scale Plot Netw.
Univ. Chic. Press Chic., 482–491.
6. Clark, J. S., Silman, M., Kern, R., Macklin, E. & Lambers, J. H. 1999 Seed dispersal near and
far: Patterns across temperate and tropical forests. Ecology 80, 1475–1494.
7. Muller-Landau, H. C., Wright, S. J., Calderón, O., Condit, R. & Hubbell, S. P. 2008
Interspecific variation in primary seed dispersal in a tropical forest. J. Ecol. 96, 653–667.
8. Zuidema, P. A., Jongejans, E., Chien, P. D., During, H. J. & Schieving, F. 2010 Integral
Projection Models for trees: a new parameterization method and a validation of model output.
J. Ecol. 98, 345–355.
9. Easterling, M. R., Ellner, S. P. & Dixon, P. M. 2000 Size-specific sensitivity: applying a new
structured population model. Ecology 81, 694–708.
Tables
Table S1. Priors for parameters in submodels.
Table S2. Parameter estimates and 95% credible intervals
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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Table S1. Priors for parameters in submodels. For normally and lognormally distributed
priors, prior 1 is the mean and prior 2 is the standard deviation, with mean and standard deviation
on the log-scale for lognormally-distributed priors. For uniform priors, prior 1 and 2 are the
minimum and maximum of the distribution, respectively.
Submodel
Seed dispersal
Seed production
Seed production
Seed production
Seed dispersal
Germination
Germination
Germination
Germination
Germination
Germination
Germination
Seedling survival
Seedling survival
Seedling survival
Seedling growth
Seedling growth
Parameter
𝑒. π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™
π‘“π‘Ÿ
𝛽0
π‘“π‘Ÿ
𝛽1
π‘“π‘Ÿ
𝛽2
π΅π‘Žπ‘‘β„Ž
π‘”π‘’π‘Ÿ
πœ‡0
𝛽 π‘”π‘’π‘Ÿ
𝛼 π‘”π‘’π‘Ÿ
𝑑𝑖𝑠. π‘”π‘’π‘Ÿ
μ𝑖𝑛.β„Žπ‘‘
π‘ π‘π‘Žπ‘™π‘’ 𝑖𝑛.β„Žπ‘‘
π‘ β„Žπ‘Žπ‘π‘’ 𝑖𝑛.β„Žπ‘‘
πœ‡0𝑠𝑠
𝛽 𝑠𝑠
𝑠𝑖𝑧𝑒 𝑠𝑠
𝑠𝑔
πœ‡0
𝛼 𝑠𝑔
Distribution
Normal
Uniform
Uniform
Uniform
Normal
Normal
Normal
Normal
Normal
Normal
Normal
Normal
Normal
Normal
Normal
Normal
Normal
Prior 1
0
0
0
-100
0
0
0
0
0
0
0
0
0
0
0
0
0
Prior 2
1.00E-06
100
100
0
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
1.00E-06
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
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Table S1 Priors for parameters in submodels, cont.
Submodel
Seedling growth
Seedling growth
Seedling growth
Seedling heightDBH allometry
Seedling heightDBH allometry
Seedling heightDBH allometry
Seedling heightDBH allometry
Seedling heightDBH allometry
Seedling heightDBH allometry
Seedling heightDBH allometry
Tree survival
Tree growth
Tree survival
Tree growth
Tree growth
Tree growth
Tree survival
Tree survival
Tree growth
Tree growth
Tree growth
Tree growth
Parameter
𝑑𝑖𝑠. 𝑠𝑔
𝑠𝑖𝑧𝑒 𝑠𝑔
𝛽 𝑠𝑔
π‘ π‘π‘Žπ‘™π‘’ 𝑠𝑔
π‘ β„Žπ‘Žπ‘π‘’ 𝑠𝑔
π‘Žβ„Žπ‘‘
𝑏 β„Žπ‘‘
𝜎 β„Žπ‘‘
π‘Ž π‘ π‘€π‘–π‘‘π‘β„Ž
𝑏 π‘ π‘€π‘–π‘‘π‘β„Ž
π‘Žπ‘ 
𝛼
𝛼 π‘Žπ‘”
𝑑𝑖𝑠. π‘Žπ‘ 
𝑑𝑖𝑠. π‘Žπ‘”
𝐺. 𝑔
𝑃. 𝑔
𝐺. 𝑠
𝑃. 𝑠
π‘Žπ‘ β„Žπ‘Žπ‘π‘’
π‘Žπ‘ π‘π‘Žπ‘™π‘’
π‘π‘ β„Žπ‘Žπ‘π‘’
π‘π‘ π‘π‘Žπ‘™π‘’
Distribution
Normal
Normal
Normal
Prior 1
0
0
0
Prior 2
1.00E-06
1.00E-06
1.00E-06
Gamma
0.01
1.00E-02
Exponential
0.01
-
Normal
0
1.00E-06
Normal
0
1.00E-06
Uniform
0
1.00E+03
Normal
0
1.00E-06
Normal
Normal
Normal
Normal
Normal
Uniform
Normal
Normal
Normal
Normal
Exponential
Normal
Normal
0
0
0
0
0
-50
0
0
0
0
1.00E-02
0
0
1.00E-06
1.00E-02
1.00E-02
1.00E-02
1.00E-02
5.00E+01
1.00E-02
1.00E-02
1.00E-02
1.00E-02
1.00E-02
1.00E-02
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
11
Table S2. Parameter estimates and 95% credible intervals
Submodel
Parameter
2.50%
50%
97.50%
Seed dispersal
Seed production
Seed production
Seed production
Seed dispersal
Germination
Germination
Germination
Germination
Germination
Germination
Germination
Seedling survival
Seedling survival
Seedling survival
Seedling growth
Seedling growth
Seedling growth
Seedling growth
Seedling growth
Seedling heightDBH allometry
Seedling heightDBH allometry
𝑒. π‘‘π‘–π‘ π‘π‘’π‘Ÿπ‘ π‘Žπ‘™
π‘“π‘Ÿ
𝛽0
π‘“π‘Ÿ
𝛽1
π‘“π‘Ÿ
𝛽2
π΅π‘Žπ‘‘β„Ž
π‘”π‘’π‘Ÿ
πœ‡0
𝛽 π‘”π‘’π‘Ÿ
𝛼 π‘”π‘’π‘Ÿ
𝑑𝑖𝑠. π‘”π‘’π‘Ÿ
μ𝑖𝑛.β„Žπ‘‘
π‘ π‘π‘Žπ‘™π‘’ 𝑖𝑛.β„Žπ‘‘
π‘ β„Žπ‘Žπ‘π‘’ 𝑖𝑛.β„Žπ‘‘
πœ‡0𝑠𝑠
𝛽 𝑠𝑠
𝑠𝑖𝑧𝑒 𝑠𝑠
𝑠𝑔
πœ‡0
𝛼 𝑠𝑔
𝑑𝑖𝑠. 𝑠𝑔
𝑠𝑖𝑧𝑒 𝑠𝑔
𝛽 𝑠𝑔
776.9
1.01
0
-0.13
0.14
-2.86
-1.29
-0.05
0.01
4.71
0.83
-0.1
-0.24
-0.06
0.1
2.81
-15.4
0.69
0.13
-0.22
1915.8
1.42
0
-0.12
0.32
-2.49
-0.8
-0.03
0.21
4.91
0.9
0
0.35
-0.04
0.14
5.46
-3.9
1.3
0.17
-0.15
4590.73
2.93
0
-0.12
0.5
-2.17
-0.39
-0.02
0.56
5.1
0.97
0.1
0.91
-0.02
0.19
8.14
-0.83
1.84
0.21
-0.08
π‘ π‘π‘Žπ‘™π‘’ 𝑠𝑔
20.62
22.17
23.79
π‘ β„Žπ‘Žπ‘π‘’ 𝑠𝑔
0.05
0.14
0.25
Caughlin T.T., Ferguson J.M., Lichstein J.W., Zuidema P.A., Bunyavejchewin S., Levey D.J.
12
Table S2. Parameter estimates and 95% credible intervals, cont.
Submodel
Parameter
2.50%
50%
97.50%
Seedling heightDBH allometry
Seedling heightDBH allometry
π‘Žβ„Žπ‘‘
-1.04
-0.85
-0.64
𝑏 β„Žπ‘‘
0.01
0.01
0.01
Seedling heightDBH allometry
𝜎 β„Žπ‘‘
0.12
0.15
0.19
Seedling heightDBH allometry
π‘Ž π‘ π‘€π‘–π‘‘π‘β„Ž
-78.42
-36.52
-14.61
Seedling heightDBH allometry
𝑏 π‘ π‘€π‘–π‘‘π‘β„Ž
6.27
15.86
34.19
Tree survival
Tree growth
Tree survival
Tree growth
Tree growth
Tree growth
Tree survival
Tree survival
Tree growth
Tree growth
Tree growth
Tree growth
𝛼 π‘Žπ‘ 
𝛼 π‘Žπ‘”
𝑑𝑖𝑠. π‘Žπ‘ 
𝑑𝑖𝑠. π‘Žπ‘”
𝐺. 𝑔
𝑃. 𝑔
𝐺. 𝑠
𝑃. 𝑠
π‘Žπ‘ β„Žπ‘Žπ‘π‘’
π‘Žπ‘ π‘π‘Žπ‘™π‘’
π‘π‘ β„Žπ‘Žπ‘π‘’
π‘π‘ π‘π‘Žπ‘™π‘’
-1.65
-0.29
0.38
1.18
-1.89
4.85
-6.79
3.17
-23.4
0.07
-19.34
0.86
-0.74
-0.15
0.82
1.56
12.75
4.92
-0.06
3.26
-9.28
0.08
0.14
0.89
-0.1
-0.04
1.21
2.06
24.38
4.98
9.05
3.37
-3.25
0.09
18.71
0.92
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