Clark, JS, C Nunes, and B Tomasek. 2019. Masting as an unreliable
resource: spatio-temporal host diversity merged with consumer movement,
storage, and diet. *Ecological Monographs*, e01381.

`mastif`

uses seed traps and crop counts on trees to
estimate seed productivity and dispersion. Attributes of individual
trees and their local environments could explain their differences in
fecundity. Inference requires information on locations of trees and seed
traps and predictors ( covariates and factors ) that could explain
source strength.

Many trees are not reproductively mature, and reproductive status is often unknown. For individuals of unknown maturation status, the maturation status must be estimated together with fecundity.

Predictors of fecundity include individual traits, site characteristics, climate, synchronicity with other trees, and lag effects. For studies that involve multiple plots and years, there can be effects of climate between sites and through time. There may be synchronicity between individuals both within and between plots.

Observations incorporate two types of redistribution. The first type is a redistribution from species to seed types. Not all seed types can be definitely assigned to species. The contribution of trees of each species to multiple seed types must be estimated.

The second redistribution from source trees to seed traps. Within a plot-year there is dependence between all seed traps induced by a redistribution kernel, which describes how seeds produced by trees are dispersed in space. Because ‘seed shadows’ of trees overlap, seeds are assigned to trees only in a probabilistic sense. The capacity to obtain useful estimates depends on the number of trees, the number of seed traps, the dispersal distances of seeds, the taxonomic specificity of seed identification, and the number of species contributing to a given seed type.

In addition to covariates and factors, the process model for fecundity can involve random tree effects, random group effects ( e.g., species-location ), year effects, and autoregressive lags limited only by the duration of data. Dispersal estimtes can include species and site differences ( Clark et al. 2013 ).

`mastif`

simulates the posterior distributions of
parameters and latent variables using Gibbs sampling, with direct
sampling, Hamiltonian Markov chain ( HMC ) updates, and Metropolis
updates. `mastif`

is implemented in R and C++ with
`Rcpp`

and `RcppArmadillo`

libraries.

`mastif`

inputsThe model requires a minimum of six inputs directly as arguments to
the function `mastif`

. There are two `formula`

s,
two `character vector`

s, and four
`data.frame`

s:

**Table 2**. Basic inputs

object | `mode` |
components |
---|---|---|

`formulaFec` |
`formula` |
fecundity model |

`formulaRep` |
`formula` |
maturation model |

`specNames` |
`character vector` |
names in column `species` of
`treeData` to include in model |

`seedNames` |
`character vector` |
names of seed types to include in model: match column
names in `seedData` |

`treeData` |
`data.frame` |
tree-year by variables, includes columns
`plot` , `tree` , `year` ,
`diam` , `repr` |

`seedData` |
`data.frame` |
trap-year by seed types, includes columns
`plot` , `trap` , `year` , one for each
`specNames` |

`xytree` |
`data.frame` |
tree by location, includes columns `plot` ,
`tree` , `x` , `y` |

`xytrap` |
`data.frame` |
trap by location, includes columns `plot` ,
`trap` , `x` , `y` |

I introduce additional inputs in the sections that follow, but start with this basic model.

Data simulation is recommended as the place to start. A simulator provides insight on how well parameters from be identified from my data. The inputs to the simulator can specify the following:

**Table 3.** Simulation inputs to
`mastSim`

`mastSim` input |
explanation |
---|---|

`nplot` |
number of plots |

`nyr` |
mean no. years per plot |

`ntree` |
mean no. trees per plot |

`ntrap` |
mean no. traps per plot |

`specNames` |
tree species codes used in `treeData`
column |

`seedNames` |
seed type codes: a column name in
`seedData` |

Most of these inputs are stochasiticized to vary structure of each
data set. Here are inputs to the simulator for a species I’ll call
`acerRubr`

:

```
<- specNames <- 'acerRubr'
seedNames <- list( nplot=5, nyr=10, ntree=30, ntrap=40, specNames = specNames, seedNames = seedNames ) sim
```

The `list sim`

holds objects needed for simulation. Here
is the simulation:

```
<- mastSim( sim ) # simulate dispersal data
inputs <- inputs$seedData # year, plot, trap, seed counts
seedData <- inputs$treeData # year, plot, tree data
treeData <- inputs$xytree # tree locations
xytree <- inputs$xytrap # trap locations
xytrap <- inputs$formulaFec # fecundity model
formulaFec <- inputs$formulaRep # maturation model
formulaRep <- inputs$trueValues # true states and parameter values trueValues
```

I first summarize these model `inputs`

generated by
`mastSim`

.

`mastSim`

`mastSim`

generates inputs needed for model fitting with
`mast`

. These objects are simulated data, including the four
`data.frame`

s ( `treeData`

, `seedData`

,
`xytree`

, `xytrap`

) and formulas (
`formulaFec`

, `formulaRep`

). Other objects are
“true” parameter values and latent states in the
`list truevalues`

used to simulate the data (
`fec`

, `repr`

, `betaFec`

,
`betaRep`

, `upar`

, `R`

). I want to see
if `mast`

can recover these parameter values for the type of
data I simulated.

Here is a mapping of objects created by `mastSim`

to the
model in Clark et al. ( 2019 ):

**Table 4.** Some of the objects from the
`list mastSim`

.

`mastSim` object |
variable | explanation |
---|---|---|

`trueValues$fec` |
\(\psi_{ij, t}\) | conditional fecundity |

`trueValues$repr` |
\(\rho_{ij, t}\) | true maturation status |

`treeData$repr` |
\(z_{ij, t}\) | observed maturation status ( with `NA`
) |

`trueValues$betaFec` |
\(\beta^x\) | coefficients for fecundity |

`trueValues$betaRep` |
\(\beta^v\) | coefficients for maturation |

`trueValues$R` |
\(\mathbf{m}\) | `specNames` to
`seedNames matrix` , rows = \(\mathbf{m}_h\) |

`seedData$active` |
in \(A_{sj, t}\) | fraction of time trap is active |

`seedData$area` |
in \(A_{sj, t}\) | trap area |

`mastSim`

assumes that predictors of maturation and
fecundity are limited to intercept and diameter. Thus, the
`formulaFec`

and `formulaRep`

are identical. Here
is fecundity:

` formulaFec`

Before fitting the model I say a bit more about input data.

`treeData`

and
`xytree`

The information on individual trees is held in the tree-years by
variables `data.frame treeData`

. Here are a few lines of
`treeData`

generated by `mastSim`

,

`head( treeData )`

`treeData`

has a row for each tree-year. Several of these
columns are required:

`data.frame treeData`

columns

`treeData` column |
explanation |
---|---|

`plot` |
plot name |

`tree` |
identifier for each tree, unique within a plot |

`year` |
observation year |

`species` |
species name |

`diam` |
diameter is a predictor for fecundity in \(\mathbf{X}\) and maturation in \(\mathbf{V}\) |

`repr` |
immature ( `0` ), mature ( `1` ),
or unknown ( `NA` ) |

There can be additional columns, but they are not required for model
fitting. The variable `repr`

is reproduction status, often
`NA`

.

There is a corresponding `data.frame xytree`

that holds
tree locations.

**Table 5.** `data.frame xytree`

columns

`xytree` column |
explanation |
---|---|

`plot` |
plot name |

`tree` |
identifier for each tree, unique within a plot |

`x, y` |
locations in the sample plot |

`xytree`

has fewer rows than `treeData`

,
because it is not repeated each year–it assumes that tree locations are
fixed. They are cross-referenced by `plot`

and
`tree`

:

`head( xytree, 5 )`

##`seedData`

and
`xytrap`

Seed counts are held in the `data.frame seedData`

as
trap-years by seed types. Here are a few lines of
`seedData`

,

`head( seedData )`

Required columns are in Table 6.

**Table 6.** `data.frame seedData`

columns

`seedData` column |
explanation |
---|---|

`plot` |
plot name |

`trap` |
identifier for each trap, unique within a plot |

`year` |
seed-crop year |

`active` |
fraction of collecting period that the trap was active |

`area` |
collection area of trap ( m\(^2\) ) |

`acerRubr` , … |
`seedNames` for columns with seed
counts |

Seed trap location data are held in the
`data.frame xytrap`

.

**Table 7.** `data.frame xytrap`

columns

`xytrap` column |
explanation |
---|---|

`plot` |
plot name |

`trap` |
identifier for each trap, unique within a plot |

`x, y` |
map location |

There is no year in `xytrap`

, because locations are
assumed to be fixed. If a seed trap location is moved during a study,
simply assign it a new trap name. Then seed counts for years when it is
not present are assigned `NA`

( missing data ) will be
imputed.

Because they are stochastic, not all simulations from
`mastSim`

generate data with sufficient pattern to allow
model fitting. I can look at the relationship between tree diameters and
seeds on a map for plot `mapPlot`

and year
`mapYear`

:

```
<- table( treeData$plot, treeData$year )
dataTab
<- which( dataTab > 0, arr.ind=T ) # a plot-year with observations
w <- w[sample( nrow( w ), 1 ), ]
w
<- as.numeric( colnames( dataTab )[w[2]] )
mapYears <- rownames( dataTab )[w[1]]
mapPlot $mapPlot <- mapPlot
inputs$mapYears <- mapYears
inputs$treeSymbol <- treeData$diam
inputs$SCALEBAR <- T
inputs
mastMap( inputs )
```

Depending on the numbers of maps I adust `treeScale`

and
`trapScale`

to see how seed accumulation compares with tree
size or fecundity. In the above map, trees are shown as green circles
and traps as gray squares. The size of the circle comes from the input
variable `treeSymbol`

, which is set to tree diameter. I could
instead set it to the ‘true’ number of seeds produced by each tree, an
output from `mastSim`

.

```
$treeSymbol <- trueValues$fec
inputs$treeScale <- 2
inputs$trapScale <- 1
inputsmastMap( inputs )
```

Which are reproductively mature? Here are true values, showing just trees that are mature:

```
$treeSymbol <- trueValues$repr
inputs$treeScale <- .5
inputsmastMap( inputs )
```

To fit the data, there must be sufficient seed traps, and sources must not be so dense such that overlapping seed shadows make the individual contributions undetectable.

Here is the frequency distribution of seeds ( observed ) and of fecundities ( unknown ) from the simulated data:

```
par( mfrow=c( 2, 1 ), bty='n', mar=c( 4, 4, 1, 1 ) )
<- inputs$seedData
seedData <- inputs$seedNames
seedNames
hist( as.matrix( seedData[, seedNames] ) , nclass=100,
xlab = 'seed count', ylab='per trap', main='' )
hist( trueValues$fec, nclass=100, xlab = 'seeds produced', ylab = 'per tree', main = '' )
```

In data of this type, most seed counts and most tree fecundities are zero.

Model fitting requires specification of the number of MCMC iterations
`ng`

and the `burnin`

. Here is an analysis using
the simulated `inputs`

from `mastSim`

with a small
number of iterations:

`<- mastif( inputs = inputs, ng = 4000, burnin = 500 ) output `

The fitted object `output`

contains MCMC chains,
estimates, and predictions, summarized in the next section.

`output`

summary, lists, and
plotsSample size, parameter estimates, goodness of fit are all provides as
tables by `summary`

.

`summary( output )`

By default, this summary is sent to the console. It can also be saved
to a `list`

, e.g.,
`outputSummary <- summary( output )`

.

`output`

The main objects returned by `mastif`

include several
lists summarized in Table 9. `parameters`

are estimated as
part of model fitting. `predictions`

are generated by the
fitted model, as predictive distributions. Note that the latent states
for log fecundity \(\psi_{ij, t}\) and
maturation state \(\rho_{ij, t}\) are
both estimated and predicted.

**Table 9.** The `list`

created by function
`mast`

.

`list` in `output` |
summary | contents |
---|---|---|

`inputs` |
from `inputs` with additions |
includes `distall` ( trap by tree distance
) |

`chains` |
MCMC chains | `agibbs` ( if random effects, the covariance
matrix \(\mathbf{A}\) ),
`bfec` ( \(\boldsymbol{\beta}^x\) ), `brep`
( \(\boldsymbol{\beta}^v\) ),
`bygibbs` ( \(\alpha_l\) or
\(\gamma_t\) if `yearEffect`
included ), `rgibbs` ( \(\mathbf{M}\) if multiple seed types ),
`sgibbs` ( \(\sigma^2\),
RMSPE, deviance ), `ugibbs` ( \(u\) parameter ) |

`data` |
data attributes | intermediate objects used in fitting, prediction |

`fit` |
diagnostics | DIC, RMSPE, scoreStates, predictScore |

`parameters` |
posterior summaries | `alphaMu` and `alphaSe` ( mean
and se for \(\mathbf{A}\), if included
), `aMu` and `aSe` ( \(\mathbf{\beta^w}_{ij}\) ),
`betaFec` ( \(\boldsymbol{\beta}^x\) ),
`betaRep` ( \(\boldsymbol{\beta}^v\) ),
`betaYrMu` and `betaYrSe` ( mean and se for year
or lag coefficients ), `upars` and `dpars` (
dispersal parameters \(u\) and \(d\) ), `rMu` and
`rSe` ( mean and se for \(\mathbf{M}\) ), `sigma` ( \(\sigma^2\) ), `acfMat` ( group
by lag empirical correlation or ACF ), `pacfMat` ( group by
lag partial correlation or PACF ), `pacfSe` ( se for
`pacfMat` ), `pacsMat` ( group by lag PACF for
seed data ) |

`prediction` |
predictive distributions | `fecPred` ( maturation \(\rho_{ij, t}\) and fecundity \(\psi_{ij, t}\) estimates and predictions ),
`seedPred` ( seed counts per trap and predictions per m\(^2\) ), `seedPredGrid`
predictions for seeds on the space-time prediction grid,
`treePredGrid` predictions for maturation and fecundity
corresponding to `seedPredGrid` . |

Prediction scores for seed-trap observations are provided in
`output$fit`

based on the estimated fecundities \([\mathbf{y} | \phi, \rho]\) as
`scoreStates`

and on the estimated parameters \([\mathbf{y} | \phi, \rho][\phi, \rho|
\boldsymbol{\beta}^x, \boldsymbol{\beta}^w, \dots]\) as
`predictScore`

. The former will be substantially higher than
the latter in cases where estimates of states \(\phi, \rho\) can be found that predict seed
data, but the variables in \(\mathbf{X},
\mathbf{V}\) do not predict those states well. These proper
scoring rules are bases on the log likelihood for the Poisson
distribution.

Predictions for a location-year prediction grid are invoked when
`predList`

is specified in the call to
`mastif`

.

`output`

Here are plots of `output`

, with the
`list plotPars`

passing the `trueValues`

for these
simulated data:

```
<- list( trueValues = trueValues )
plotPars mastPlot( output, plotPars )
```

Because this is a simulated data set, I pass the
`trueValues`

in the `list plotPars`

.

By inspecting chains I decide that it is not converged and continue,
with `output`

from the previous fit being the new
`inputs`

:

`<- mastif( inputs = output, ng = 5000, burnin = 3000 ) output `

Other arguments passed to `mastPlot`

in the
`list plotPars`

are given as examples below and listed at
`help( mastPlot )`

.

`mastPlot`

generates the following plots:

`maturation`

: chains for maturation parameters in \(\beta^v\).`fecundity`

: chains for fecundity parameters in \(\beta^x\).`dispersal parameter`

: chains for dispersal parameter \(u\).`variance sigma`

: chains for error variance \(\sigma^2\), RMSPE, and deviance.`maturation, fecundity`

: posterior 68% ( boxes ) and 95% ( whiskers ) for \(\beta^x\) and \(\beta^v\).`maturation, fecundity by diameter`

: estimates ( dots ) with \(95%\) predictive means for latent states.`seed shadow`

: with 90% predictive interval`prediction`

: seed data predicted from estimates of latent maturation and fecundity ( a ) and from parameter estimates. If`trueValues`

are supplied from`mastSim`

, then panel ( c ) includes true versus predicted values. There is an important distinction between ( a ) and ( b )–good predictions in ( a ) indicate that combinations of seed sources can be found to predict the seed data, without necessarily meaning that the process model can predict maturation and fecundity. Good predictions in ( b ) face the steeper challenge that the process model must predict both maturation and fecundity, which, in turn, predict seed rain.`parameter recovery`

: if`trueValues`

are supplied from`mastSim`

, then this plot is provided comparing true and estimated values for \(\beta^v\) and \(\beta^x\).`predicted fecundity, seed data`

: maps show predicted fecundity of trees ( sizes of green circles ) with seed data ( gray squares ). If`predList`

is supplied to`mastif`

, then the predicted seed surface is shown as shaded contours.`partial ACF`

: autocorrelation function for fecundity ( estimated ) ( a ) and in seed counts ( observed ) ( b ).`tree correlation in time`

: pairwise correlations between trees on the same plot.

The plots displayed by `mastPlot`

include the MCMC chains
that are not yet converged. Again, I can restart where I left off by
using `output`

as the `inputs`

to
`mast`

. In addition, I predict the seed surface from the
fitted model for a plot and year, as specified in
`predList`

.

```
$predList <- list( mapMeters = 3, plots = mapPlot, years = mapYears )
inputs<- mastif( inputs = output, ng = 2000, burnin = 1000 ) output
```

To look closer at the predicted plot-year I generate a new map:

```
$mapPlot <- mapPlot
output$mapYears <- mapYears
output$treeScale <- 1.5
output$trapScale <- .8
output$PREDICT <- T
output$scaleValue <- 20
output$plotScale <- 1
output$COLORSCALE <- T
output$LEGEND <- T
output
mastMap( output )
```

The maps show seed counts ( squares ) and fecundity predictions ( circles ). For predicted plot years there is also shown a seed prediction surface. The surface is seeds per m\(^2\).

Depending on the simulation, convergence may require more iterations.
The partial autocorrelation for years should be weak, because none are
simulated in `mastSim`

. However, actual data will contain
autocorrelation. The fecundity-time correlations show modal values near
zero, because simulated data do not include individual covariance.
Positive spatial covariance is imposed by dispersal.

To send output to a single `Rmarkdown`

file and
`html`

or `pdf`

, I use this:

```
$RMD <- 'pdf'
plotParsmastPlot( output, plotPars )
```

This option will generate a file `mastifOutput.Rmd`

, which
can be opened in Rstudio, edited, and knitted to `pdf`

format. It contains data and posterior summaries generated by
`summary`

and `mastPlot`

. This pdf will not
include stand maps. Maps will be included in the `html`

version, obtained by setting `plotPars$RMD <- 'html'`

.

Seed shadow models confront convoluted likelihood surfaces, in the sense that we expect local optima. These surfaces are hard to traverse with MCMC ( and impossible with HMC ), because maturation status is a binary state that must be proposed and accepted together with latent fecundity. Posterior simulation can get bogged down when fecundity estimates converge for a combination of mature and immature trees that is locally but not globally optimal. Especially when there are more trees of a species than there are seed traps, we expect many iterations before the algorithm can ‘find’ the specific combination of trees that together best describe the specific combination of seed counts in many seed traps. Compounding the challenge is the fact that, because both maturation and fecundity are latent variables for each individual, the redistribution kernel must be constructed anew at each MCMC step. Yet, analysis of simulated data shows that convergence to the correct posterior distribution is common. It just may depend on finding reasonable prior parameter values ( see below ) and long chains.

Examples in this vignette assign enough interations to show this
progress toward convergence may be happening, but sufficiently few to
avoid long waiting times. To evaluate convergence, consider the plots
for chains of `sigma`

( the residual variance \(\sigma\) on log fecundity ), the
`rspse`

( the seed count residual ), and the
`deviance`

. Finally, the plot of seed observed vs predicted
gives a sense of progress.

As demonstrated above, restart `mastif`

with the fitted
object.

Often a seed type could have come from trees of more than one
species. Seeds that are only identified to genus level include in
`seedNames`

the `character`

string
`UNKN`

. In this simulation the three species
`pinuTaeda`

, `pinuEchi`

, and `pinuVirg`

contribute most seeds to the type `pinuUNKN`

.
**Important:** there can be only one element in
`seedNames`

containing the string `UNKN`

.

Here are some inputs for the simulation:

```
<- c( 'pinuTaeda', 'pinuEchi', 'pinuVirg' )
specNames <- c( 'pinuTaeda', 'pinuEchi', 'pinuVirg', 'pinuUNKN' )
seedNames <- list( nyr=4, ntree=25, nplot=10, ntrap=50, specNames = specNames,
sim seedNames = seedNames )
```

There is a `specNames`

-by-`seedNames`

matrix
`M`

that is estimated as part of the posterior distribution.
For this example `seedNames`

containing the string
`UNKN`

refers to a seed type that cannot be differentiated
beyond the level of the genus `pinu`

.

Here is the simulation with output objects with 2/3 of all seeds identified only to genus level:

```
<- mastSim( sim ) # simulate dispersal data
inputs <- inputs$trueValues$R # species to seedNames probability matrix
R round( R, 2 )
```

The matrix `M`

stacks the length-\(M\) vectors \(\mathbf{m}'_s\) discussed in Clark et
al. ( 2019 ) as a species-by-seed type matrix. There is a matrix for
each plot, here stacked as a single matrix. This is the matrix of values
used in simulation. `mastif`

will estimate this matrix as
part of the posterior distribution.

Here is a model fit:

`<- mastif( inputs = inputs, ng = 2000, burnin = 1000 ) output `

The model summary now includes estimates for the unknown
`M`

as the “species to seed type matrix”:

`summary( output )`

Output plots will include chains for estimates in `M`

.
There will also be estimates for each species included in
`specNames`

:

```
<- list( trueValues = inputs$trueValues )
plotPars mastPlot( output, plotPars )
```

The inverse of \(\mathbf{M}\) is the
probability that an unknown seed of type \(m\) was produced by a tree of species \(s\). These estimates are included in the
plot `Species to undiff seed`

.

Again, the `.Rmd`

file can be knitted to a
`pdf`

file.

Here is a restart, now with `plots`

and `years`

specified for prediction in `predList`

:

```
<- with( inputs$seedData, table( plot, year ) )
tab <- as.numeric( colnames( tab )[tab[1, ] > 0] ) # years for 1st plot
years $predList <- list( plots = 'p1', years = years )
output<- mastif( inputs = output, ng = 3000, burnin = 1500 )
output mastPlot( output )
```

Chains for the `matrix M`

will converge for plots where
there are sufficient trees and seeds to obtain an estimate. They will
not be identified on plots where one or the other are rare or
absent.

`specNames`

and
`seedNames`

In the many data sets where seeds of multiple species are not
differentiated the undifferentiated seed type occupies a column in
`seedData`

having a column name that includes the string
`UNKN`

. For a concrete example, if `specNames`

on
a plot include trees in `treeData$species`

with the
`specNames pinuTaed`

and `pinuEchi`

, then many
seeds might be indentified as `seedNames pinuUNKN`

. In the
foregoing example, estimates of the `matrix M`

reflect the
contributions of each species to the `UNKN`

type. This could
be specified in several ways:

```
<- c( 'pinuTaed', 'pinuEchi' )
specNames
#seeds never differentiated:
<- c( 'pinuUNKN' )
seedNames
#one species sometimes differentiated:
<- c( 'pinuTaed', 'pinuUNKN' )
seedNames
#both species sometimes differentiated:
<- c( 'pinuTaed', 'pinuEchi', 'pinuUNKN' ) seedNames
```

`mastPlot`

written to
filesThe `function mastPlot`

generates summary plots of
`output`

. The user has access to all objects used to generate
these plots, as discussed in the previous section. By default plots in
`mastPlot`

can be rendered to the console. If
`plotPars$SAVEPLOTS = T`

is included in the
`list plotPars`

passed to `mastPlot`

, then each
plot is saved to a `.pdf`

file. Plots can be consolidated
into a single `.Rmd`

file, which can be knitted to
`.html`

or `.pdf`

with
`plotPars$RMD = html`

or `plotPars$RMD = pdf`

.

For illustration I use sample data analyzed by Clark et al. ( 2013 ), with data collection that has continued through 2017. It consists of multiple years and sites.

Here I load data for species with a single recognized seed type,
*Liriodendron tulipifera*. Here is a map, with seed traps scaled
by seed counts, and trees scaled by diameter,

```
library( repmis )
<- "https://github.com/jimclarkatduke/mast/blob/master/liriodendronExample.rData?raw=True"
d ::source_data( d )
repmis<- list( treeData = treeData, seedData = seedData,
mapList specNames = specNames, seedNames = seedNames,
xytree = xytree, xytrap = xytrap, mapPlot = 'DUKE_BW',
mapYears = 2011:2014, treeSymbol = treeData$diam,
treeScale = .7, trapScale = 1.5, plotScale = 2,
SCALEBAR=T, scaleValue=50 )
mastMap( mapList )
```

Here are a few lines of `treeData`

, which has been trimmed
down to this single species,

`head( treeData, 3 )`

Here are a few lines of `seedData`

,

`head( seedData, 3 )`

Here I fit the model.

```
<- as.formula( ~ diam ) # fecundity model
formulaFec <- as.formula( ~ diam ) # maturation model
formulaRep
<- list( specNames = specNames, seedNames = seedNames,
inputs treeData = treeData, seedData = seedData, xytree = xytree,
xytrap = xytrap )
<- mastif( inputs, formulaFec, formulaRep, ng = 3000, burnin = 1000 ) output
```

Following this short sequence, I fit a longer one and predict one of the plots:

```
$predList <- list( mapMeters = 10, plots = 'DUKE_EW', years = 2010:2015 )
output<- mastif( inputs = output, ng = 4000, burnin = 1000 ) output
```

Here are some plots followed by comments on display panels. Notice that when it progresses to the maps for plot DUKE_HW, they will include the predicted seed shadows:

`mastPlot( output )`

From `fecundity`

chains, still more iterations are needed
for convergence.

From `seed shadow`

, seed rain beneath a 30-cm diameter
tree averages near 0.2 seeds per m\(^2\).

Although a combination of maturation/fecundity can be found to
predict the seed data in `prediction`

( part a ), the process
model does not well predict the maturation/fecundity combination ( part
b ). In other words, the maturation/fecundity/dispersal aspect of the
model is effective, whereas the design does not yet include variables
that help explain maturation/fecundity.

From the many maps in `predicted fecundity, seed data`

,
note that the `DUKE_EW`

site includes prediction surfaces, as
specfied in `predList`

.

Here is the summary:

`summary( output )`

At this point in the the Gibbs sampler, the DIC and root mean square prediction error are:

`$fit output`

As mentioned above, prediction scores for seed-trap observations are
based on the estimated fecundities \([\mathbf{y} | \phi, \rho]\) as
`scoreStates`

and on the estimated parameters \([\mathbf{y} | \phi, \rho][\phi, \rho|
\boldsymbol{\beta}^x, \boldsymbol{\beta}^w, \dots]\) as
`predictScore`

. The `TGc`

and `TGd`

parameters are the affine-transformation parameters ( intercept, slope )
relating the predictive variance to the error variance ( Thorarinsdottir
and Gneiting, 2010 ).

Individual ( tree differences ) can be random and year-to-year
differences can be fixed; the latter are not ‘exchangeble’. In cases
where there are no predictors that explain variation among individuals
the `formula`

can be limited to an intercept, using
`~ 1`

. In this case, it can be valuable to estimate fecundity
even when there are no good predictors. For this intercept-only model,
random effects and/or year effects can allow for variation. Prior
parameter values are supplied as discussed below.

```
#group plots in regions for year effects
<- rep( 'sApps', nrow( treeData ) )
region as.character( treeData$plot ) == 'DUKE_EW' ] <- 'piedmont'
region[
$region <- region
treeData
<- as.formula( ~ diam )
formulaFec <- as.formula( ~ diam )
formulaRep <- list( groups = 'region' )
yearEffect <- list( randGroups = 'treeID', formulaRan = as.formula( ~ 1 ) )
randomEffect <- list( specNames = specNames, seedNames = seedNames,
inputs treeData = treeData, seedData = seedData,
xytree = xytree, xytrap = xytrap,
priorDist = 28, priorVDist = 15, maxDist = 50, minDist = 15,
minDiam = 25, maxF = 1e+6,
randomEffect = randomEffect, yearEffect = yearEffect )
<- mastif( inputs, formulaFec, formulaRep, ng = 2000, burnin = 1000 )
output mastPlot( output )
```

Without predictors, the fitted variation is coming from random effects and year effects.

To substitute year effects for AR( \(p\) ) effects, simply remove the argument
specification of `p`

in the `yearEffect list`

:

`<- list( groups = c( 'species', 'region' ) ) # year effects yearEffect `

In previous examples, the prior parameter values were past in the
`list inputs`

. I can also specify prior values as inputs
through the `inputs$priorList`

or
`inputs$priorTable`

holding parameters named in Table 8.

**Table 8.** Components of `inputs`

with
default values.

object | explanation |
---|---|

`priorDist = 25` |
prior mean dispersal distance parameter ( \(m\) ) |

`priorVDist = 40` |
prior variance dispersal parameter |

`minDist = 4` |
minimum mean dispersal distance ( \(m\) ) |

`maxDist = 70` |
maximum mean dispersal distance ( \(m\) ) |

`maxF = 1e+8` |
maximum fecundity ( seeds per tree-year ) |

`minDiam = 10` |
minimum `diam` below which a tree can mature
( \(cm\) ) |

`maxDiam = 40` |
maximum `diam` above which a tree can be
immature ( \(cm\) ) |

`sigmaMu = 1` |
prior mean residual variance \(\sigma^2\) |

`sigmaWt = sqrt( nrow( treeData ) )` |
weight on prior mean ( no. of observations ) |

The mean and variance of the dispersal kernel, `priorDist`

and `priorVDist`

, refer to the dispersal parameter \(u\), transformed to the mean distance for
the dispersal kernel. The parameters `minDist`

and
`maxDist`

place minimum and maximum bounds on \(d\).

Fecundity \(\phi\) has a prior maximum
value of `maxF`

.

`minDiam`

and `maxDiam`

bound diameter ranges
where a tree of unknown maturation status can be mature or not. This
prior range is overridden by values in the `treeData$repr`

column that establish an observed maturation state for a tree-year ( 0 -
immature, 1 - mature ).

In general, large-seeded species, especially those that can be
dispersed by vertebrates, generate noisy seed-trap data, despite the
fact that the bulk of the counts still occur close to the parent, and
the mean dispersal distance is relatively low. Large-seeded species
produce few fruits/seeds. Long-distance dispersal cannot be estimated
from inventory plots, regardless of plot size, because the fit is
dominated by locally-derived seed. Consider values for maximum fecundity
as low as `maxF = 10000`

, minimum dispersal
`minDist = 2`

, and maximum dispersal
`maxDist = 12`

. Recall that the latter values refer to the
dispersal kernel parameter value, not the maximum distance a seed can
travel, which is un-constrained.

Prior parameter values can be passed as a `list`

,
e.g.,

`$priorList <- list( minDiam = 15, maxDiam = 60 ) inputs`

Alternatively, prior parameter values can be passed as a table, with
parameters for column names for `specNames`

for rownames.
Here is a file holding parameter values and the
`function mastPriors`

to obtain a table for several species
in the genus \(Pinus\),

```
<- "https://github.com/jimclarkatduke/mast/blob/master/priorParametersPinus.csv?raw=True"
d download.file( d, destfile="priorParametersPinus.csv" )
<- c( "pinuEchi", "pinuRigi", "pinuStro", "pinuTaed", "pinuVirg" )
specNames <- c( "pinuEchi", "pinuRigi", "pinuStro", "pinuTaed", "pinuVirg", "pinuUNKN" )
seedNames <- mastPriors( "priorParametersPinus.csv", specNames,
priorTable code = 'code4', genus = 'pinus' )
```

The argument `code = 'code8'`

specifies the column in
`priorParametersPinus.csv`

holding the codes corresponding to
`specNames`

. In `mastif`

the format
`code4`

means that names consist of the first 4 letters from
the genus and species, like this: `pinuTaed`

. The
`genus`

is provided to allow for genus-level parameters in
cases where priors for individual species have not been specified in
`priorParametersPinus.csv`

.

For coefficients in fecundity, `betaPrior`

specifies
predictor effects by sign. The use of prior distributions that are flat,
but truncated, is two-fold ( Clark et al. 2013 ). First, where prior
information exists, it often is limited to a range of values. For
regressions coefficients ( e.g., \(\boldsymbol{\beta}\) ) we typically have a
prior belief about the sign of the effect ( positive or negative ), but
not its magnitude or appropriate weight. Second, within bounds placed by
the prior, the posterior has the shape of the likelihood, unaffected by
a prior weight. Prior weight is hard to specify sensibly for this
hierarchical, non-linear model.

Here is an example using `betaPrior`

to specify a
quadratic diameter effect. First, here is a data set for
*Pinus*:

```
<- "https://github.com/jimclarkatduke/mast/blob/master/pinusExample.rdata?raw=True"
d ::source_data( d ) repmis
```

Here I specify formulas, prior bounds for `diam`

(
quadratic ), and fit the model:

```
<- as.formula( ~ diam )
formulaRep <- as.formula( ~ diam + I( diam^2 ) )
formulaFec <- list( pos = 'diam', neg = 'I( diam^2 )' )
betaPrior
<- list( treeData = treeData, seedData = seedData, xytree = xytree,
inputs xytrap = xytrap, specNames = specNames, seedNames = seedNames,
betaPrior = betaPrior, priorTable = priorTable,
seedTraits = seedTraits )
<- mastif( inputs = inputs, formulaFec, formulaRep,
output ng = 500, burnin = 200 )
# restart
<- mastif( output, formulaFec, formulaRep, ng = 5000, burnin = 1000 )
output mastPlot( output )
```

Here again, many of the seed ID maxtrix elements are well identified
( trace plots labeled “`M matrix plot`

”, others are uncertain
due to small numbers of the different species that could contribute to a
seed type. These are presented as bar and whisker plots for elements of
matrix \(\mathbf{M}\) ( fraction of
seed from a species that is counted as each seed type ) in the plot
labeled `species -> seed type`

. Bar plots show the
fraction of unknown seeds that derive from each species, labeled
`species -> seed type`

. The distribution of diameters in
the data will limit the ability to estimate its effect on maturation and
fecundity.

Note that the estimates for fecundity coefficients, \(\boldsymbol{\beta}^x\), are positive for
`diam`

and negative for `diam^2`

. If there is no
evidence in the data for a decrease \(\frac{\partial{\psi}}{\partial{diam}}\),
then the quadratic term is near zero. In this case, the predicted
fecundity in the plot labelled
`maturation, fecundity by diameter`

will increase
exponentially.

Most individuals produce no seed, due to resource limitation,
especially light, in crowded stands. As trees increase in size and
resource access they mature, and become capable of seed production.
Maturation is hard to observe, so it must be modelled. In our data sets,
maturation status is observed, but most values are NA; it is only
assigned if certain. A value of 1 means that reproduction is observed. A
value of 0 means that the entire crown is visible during the fruiting
season, and it is clear that no reproduction is present. Needless to
say, most observations from beneath closed canopies are NA. The
observations are entered in the column `repr`

in the
`data.frame treeData`

. Above I showed an example where
`minDiam`

is set as a prior that trees of smaller diameters
are immature and `maxDiam`

is the prior that trees above this
diameter are mature.

`mastif`

further admits estimates of cone production. The
column `treeData$cropCount`

refers to the cones that will
open and contribute to trap counts in the year
`treeData$year`

. There is another column
`treeData$cropFraction`

, which refers to the fraction of the
tree canopy that is represented by the cone count. When crop counts are
used, a `matrix seedTraits`

must be supplied with one row per
species and a column with seeds per fruit, cone, or pod. The rownames of
`seedTraits`

are the `specNames`

. The colname of
`seedTraits`

with seeds per fruit is labeled
`seedsPerFruit`

.

Seed studies often include seed collections in years when trees are
not censused. For example, tree data might be collected every 2 to 5
years, whereas seed data are available as annual counts. In this case,
there there are years in `seedData$year`

that are missing
from `treeData$year`

. `mastif`

needs a tree year
for each trap year. If tree data are missing from some trap years, I
need to constuct a complete `treeData data.frame`

that
includes these missing years. This amended version of
`treeData`

must be accessible to the user, to allow for the
addition of covariates such as weather variables, soil type, and so
forth.

The function `mastFillCensus`

allows the user to access
the filled-in version of `treeData`

that will be fitted by
`mastif`

. `mastFillCensus`

accepts the same
`list`

of `inputs`

that is passed to the function
`mastif`

. The missing years are inserted for each tree with
interpolated diameters. The `list inputs`

is returned with
objects updated to include the missing census years and modified
slightly for analysis by `mastif`

.
`inputs$treeData`

can now be annotated with the covariates
that will be included in the model. Here is the example from the
`help`

file. First I read a file that has complete years, so
I randomly remove years:

```
# randomly remove years for this example:
<- sort( unique( treeData$year ) )
years <- sample( years, 5 )
sy <- treeData[treeData$year %in% sy, ]
treeData 1:10, ] treeData[
```

Note the missing years, as is typical of mast data sets. Here is the file after filling missing years:

```
<- list( specNames = specNames, seedNames = seedNames,
inputs treeData = treeData, seedData = seedData,
xytree = xytree, xytrap = xytrap, priorTable = priorTable,
seedTraits = seedTraits )
<- mastFillCensus( inputs, beforeFirst=10, afterLast=10 )
inputs $treeData[1:10, ] inputs
```

The missing `plotYr`

combinations in `treeData`

have been filled to match thos in `seedData`

. Now columns can
be added to `inputs$treeData`

, as needed in
`formulaFec`

or `formulaRep`

.

In cases where tree censuses start after seed trapping begins or tree
censuses end before seed trapping ends, it may be reasonable to assume
that the same trees are producing seed in those years pre-trapping or
post-trapping years. In these cases, `mastFillCensus`

can
accommodate these early and/or late seed trap data by extrapolating
`treeData`

`beforeFirst`

years before seed
trapping begins or `afterLast`

years after seed tapping
ends.

Continuing with the \(Pinus\) example, here I want to add covariates for missing years as needed for an AR( \(p\) ) model, in this example \(p\) = 4. First, consider the tree-years included in this sample, before and after in-filling:

```
# original data
table( treeData$year )
# filled census
table( inputs$treeData$year )
table( seedData$year )
```

Note that the infilled version of tree data in the
`list inputs`

has the missing years, corresponding to those
included in `seedData`

. Here I set up the year effects model
and infill to allow for `p = 3`

,

```
<- 3
p <- mastFillCensus( inputs, p = p )
inputs <- inputs$treeData treeData
```

Here are regions for random effects in the AR( 3 ) model:

```
<- c( 'CWT', 'DUKE', 'HARV' )
region $region <- 'SCBI'
treeDatafor( j in 1:length( region ) ){
<- which( startsWith( treeData$plot, region[j] ) )
wj $region[wj] <- region[j]
treeData
}$treeData <- treeData
inputs<- list( groups = c( 'species', 'region' ), p = p ) yearEffect
```

I add the climatic deficit ( monthly precipitation minus PET ) as a covariant. First, here is a data file,

```
<- "https://github.com/jimclarkatduke/mast/blob/master/def.csv?raw=True"
d download.file( d, destfile="def.csv" )
```

The format for the file `dev.csv`

is `plot`

by
`year_month`

. I have saved it in my local directory. The
function `mastClimate`

returns a `list`

holding
three vectors, each having length equal to
`nrow( treeData )`

. Here is an example for the cumulative
moisture deficit for the previous summer. I provide the file name, the
vector of plot names, the vector of previous years, and the months of
the year. To get the cumulative deficit, I use
`FUN = 'sum'`

:

```
<- inputs$treeData
treeData <- mastClimate( file = 'def.csv', plots = treeData$plot,
deficit years = treeData$year - 1, months = 6:8,
FUN = 'sum', vname='def' )
<- cbind( treeData, deficit$x )
treeData summary( deficit )
```

The first column in `deficit`

is the variable itself for
each tree-year. The second column holds the site mean value for the
variable. The third column is the difference between the first two
columns All three can be useful covariates, each capturing different
effects ( Clark et al. 2014 ). I could append any or all of them as
columns to `treeData`

.

Here is an example using minimum temperature of the preceeding
winter. I obtain the minimum with two calls to `mastClimate`

,
first for Dec of the previous year (
`years = treeData$year - 1, months = 12`

), then from Jan,
Feb, Mar for the current year (
`years = treeData$year, months = 1:3`

). I then take the
minimum of the two values:

```
# include min winter temperature
<- "https://github.com/jimclarkatduke/mast/blob/master/tmin.csv?raw=True"
d download.file( d, destfile="tmin.csv" )
# minimum winter temperature December through March of previous winter
<- mastClimate( file = 'tmin.csv', plots = treeData$plot,
t1 years = treeData$year - 1, months = 12, FUN = 'min',
vname = 'tmin' )
<- mastClimate( file = 'tmin.csv', plots = treeData$plot,
t2 years = treeData$year, months = 1:3, FUN = 'min',
vname = 'tmin' )
<- apply( cbind( t1$x[, 1], t2$x[, 1] ), 1, min )
tmin $tminDecJanFebMar <- tmin
treeData$treeData <- treeData inputs
```

Here is a model using several of these variables:

```
<- as.formula( ~ diam )
formulaRep <- as.formula( ~ diam + defJunJulAugAnom + tminDecJanFebMar )
formulaFec $yearEffect <- yearEffect
inputs<- mastif( inputs = inputs, formulaFec, formulaRep, ng = 2500, burnin = 1000 ) output
```

Data for future years can be a scenario, based on assumptions of status quo in the mean and variance, an assumed rate of climate change, and so on.

Seed production is volatile, with order of magnitude variation from year-to-year. There is synchronicity among individuals of the same species, the “masting” phenomenon. There are large difference between individuals, that are not explained by environmental variables. In this section I discuss extensions to random effects, year effects, lag effects, and fitting multiple species having seed types that are not always identifiable to species.

Random individual effects currently can include random intercepts for the fecundities of each individual tree that is imputed to be in the mature state for at least 3 years. [There are no random effects on maturation, because they would be hard to identify from seed trap data for this binary response.]

I include in the `inputs list`

the
`list randomEffect`

, which includes the column name for the
random group. Typically this would be a unique identifier for a tree
within a plot, e.g., `randomEffect$randGroups = 'tree'`

.
However, `randGroups`

could be the plot name. This column is
interpreted as a `factor`

, each level being a group. Random
effects will not be fitted on individuals that are in the mature state
less than 3 years.

The `formulaRan`

is the random effects model. Because
individual time series tend to short, it is currently implemented only
for intercepts. Here is a fit with random effects.

```
<- as.formula( ~ diam ) # fecundity model
formulaFec <- as.formula( ~ diam ) # maturation model
formulaRep $randomEffect <- list( randGroups = 'tree', formulaRan = as.formula( ~ 1 ) )
inputs<- mastif( inputs = inputs, formulaFec, formulaRep, ng = 2000, burnin = 1000 ) output
```

Here is a restart:

```
<- mastif( inputs = output, ng = 4000, burnin = 1000 )
output mastPlot( output )
```

There is a new panel for `fixed plus random effects`

,
showing the individual combinations of intercepts.

- the
`prediction`

panel ( b ) shows some improvement, indicating that even with random effects, diameter struggles to predict maturation/fecundity.

`$fit output`

As discussed previously, the model admits year effects and lag effects, the latter as an AR( \(p\) ) model. Year effects assign a coefficient to each year \(t = [1, \dots, T_j]\). Lag effects assign a coefficient to each of \(j \in \{1, \dots, p\}\) plags, where the maximum lag \(p\) should be substantially less than the number of years in the study. Year effects can be organized in random groups. Specification of random groups is done in the same way for year effects and for lag effects.

I define random groups for year and lag effects by species, by plots,
or both. When there are multiple species that contribute to the modeled
seed types, I expect the year effects to depend on which species is
actually producing the seed. When there are multiple plots sufficiently
distant from one another, I might allow for the fact that year effects
or lag effects differ by group; `yearEffect$groups`

allows
that they need not mast in the same years. In the example below, I’ll
use the term *region* for plots in the same plotGroup.

Here is a breakdown for this data set by region:

`with( treeData, colSums( table( plot, region ) ) )`

Here are year effects structured by random groups of plots, given by
the column `region`

in `treeData`

:

`<- list( groups = c('species', 'region' ) ) yearEffect `

This option will fit a year effect for both provinces and years having sufficient individuals estimated to be in the mature state. Here is the model with random year effects,

\[\log \psi_{ij, t} \sim N \left(
\mathbf{x}'_{ij, t} \mathbf{\beta}^x + \gamma_t + \gamma_{g[i], t},
\sigma^2 \right )\] where the year effect \(\gamma_{g[i], t}\) is shared by trees in
all plots defined by `yearEffect$province`

, \(ij \in g\). Year effects are sampled
directly from conditional posteriors.

```
$treeData <- treeData
inputs$randomEffect <- randomEffect
inputs$yearEffect <- yearEffect
inputs<- mastif( inputs = inputs, formulaFec, formulaRep, ng = 2500, burnin = 500 ) output
```

Here is a restart, with predictions for one of the plots:

```
<- list( mapMeters = 10, plots = 'DUKE_BW', years = 1998:2014 )
predList $predList <- predList
output<- mastif( inputs = output, ng = 3000, burnin = 1000 )
output mastPlot( output )
```

Note that still more iterations are needed for convergence. Here are
some comments on `mastPlot`

:

In the

`dispersal parameter u`

panel there are now year effects plotted for the two random groups`mtn`

and`piedmont`

.The subsequent panel

`dispersal mean and variance`

shows the mean and variance of random effectsThere is a

`dispersal by group`

panel showing posterior estimate for the two random groups, with scales for the parameter \(u\) on the left ( m\(^2\) ) and mean parameter \(d\) on the right ( m ).There has been some improvement in the

`prediction`

, panel ( b ).The

`predicted fecundity, seed data`

maps for the plot`DUKE_BW`

show seed prediction surfaces.The

`year effect groups`

shows year effects for random groups in`treeData$region`

.`partial ACF`

shows partial autocorrelation by species and plot.

Most data sets have multiple seed types that complicate estimation of
mast production by each species. This example considers *Pinus*
spp, seeds of which cannot be confidently assigned to species. Here I
load the data and generate a sample of maps from several years,
including all species and seed types.

```
<- "https://github.com/jimclarkatduke/mast/blob/master/pinusExample.rdata?raw=True"
d ::source_data( d )
repmis
<- list( treeData = treeData, seedData = seedData,
mapList specNames = specNames, seedNames = seedNames,
xytree = xytree, xytrap = xytrap, mapPlot = 'DUKE_EW',
mapYears = c( 2007:2010 ), treeSymbol = treeData$diam,
treeScale = .6, trapScale=1.4,
plotScale = 1.2, LEGEND=T )
mastMap( mapList )
```

Note the tendency for high seed accumulation ( large green squares ) near dense, large trees ( large brown circles ).

In this example, I again model seed production as a function of log
diameter, `diam`

, now for multiple species and seed types.
This is an AR( p ) model, because I include the number of lag terms
`yearEffect$p = 5`

,

\[\log \psi_{ij, t} \sim N \left( \mathbf{x}'_{ij, t} \mathbf{\beta}^x + \sum^p_{l=1} ( \alpha_l + \alpha_{g[i], l} ) \psi_{ij, t-l}, \sigma^2 \right )\] Only years \(p < t \le T_i\) are used for fitting. Samples are drawn directly from the conditional posterior distribution.

In the table printed at the outset are trees by plot and year, i.e.,
the `groups`

assigned in `inputs$yearEffect`

. The
zeros indicate either absence of trees or that no plots were sampled in
those years. ( These are not the same thing, `mastif`

knows
the difference ).

In the code below I specify formulas, AR( \(p\) ), and random effects, and some prior values. Due to the large number of trees, convergence is slow. Because I do not assume that trees of different species necessarily mast in the same years, I allow them to differ through random groups on the AR( \(p\) ) terms.

```
<- as.formula( ~ diam ) # fecundity model
formulaFec <- as.formula( ~ diam ) # maturation model
formulaRep
<- list( groups = 'species', p = 4 ) # AR( 4 )
yearEffect <- list( randGroups = 'tree',
randomEffect formulaRan = as.formula( ~ 1 ) )
<- list( specNames = specNames, seedNames = seedNames,
inputs treeData = treeData, seedData = seedData,
yearEffect = yearEffect,
randomEffect = randomEffect,
xytree = xytree, xytrap = xytrap, priorDist = 20,
priorVDist = 5, minDist = 15, maxDist = 30,
minDiam = 12, maxDiam = 40,
maxF = 1e+6, seedTraits = seedTraits )
<- mastif( inputs = inputs, formulaFec, formulaRep, ng = 500, burnin = 100 ) output
```

Here is a restart:

```
<- mastif( inputs = output, ng = 3000, burnin = 1000 )
output mastPlot( output, plotPars = plotPars )
```

Again, convergence will require more iterations. The AR( \(p\) ) coefficients in the
`lag effect group`

panel shows the coefficients by random
group. They are also shown in a separate panel, with each group plotted
separately. In the `ACF eigenvalues`

panel are shown the
eigenvalues for AR lag coefficients on the real ( horizontal ) and
imaginary ( vertical ) scales with the unit circle, within which
oscillations are damped. The imaginary axis describes oscillations.

Here’s a restart with predictions:

```
<- c( 'DUKE_EW', 'CWT_118' )
plots <- 1980:2025
years $predList <- list( mapMeters = 10, plots = plots, years = years )
output<- mastif( inputs = output, ng = 3000, burnin = 1000 ) output
```

and updated plots:

`mastPlot( output, )`

Note that convergence requires additional iterations ( larger
`ng`

). The predictions of seed production will progressively
improve with convergence.

```
<- output
mapList $mapPlot <- 'DUKE_EW'
mapList$mapYears <- c( 2011:2012 )
mapList$PREDICT <- T
mapList$treeScale <- .5
mapList$trapScale <- .8
mapList$LEGEND <- T
mapList$scaleValue <- 50
mapList$plotScale <- 2
mapList$COLORSCALE <- T
mapList$mfrow <- c( 2, 1 )
mapList
mastMap( mapList )
```

Or a larger view of a single map:

```
$mapPlot <- 'CWT_118'
mapList$mapYears <- 2015
mapList$PREDICT <- T
mapList$treeScale <- 1.5
mapList$trapScale <- .8
mapList$LEGEND <- T
mapList$scaleValue <- 50
mapList$plotScale <- 2
mapList$COLORSCALE <- T
mapList$mfrow <- c( 1, 1 )
mapListmastMap( mapList )
```

Here is a summary of parameter estimates:

`summary( output )`

R code is highly vectorized. Unavoidable loops are written in C++ and
exploit the C++ library `Armadillo`

, available through
`RcppArmadillo`

. Alternating with Metropolis are Hamiltonian
MC steps to encourage large movements.

Despite extensive vectorization and C++ for cases where loops are unavoidable, convergence can be slow. A collection of plots inventoried over dozens of years can generate in excess of \(10^6\) tree-year observations and \(10^4\) trap year observations. There is no escaping the requirement of large numbers of indirectly sampled latent variables. If random effects are included, there are ( obviously ) as many random groups as there are trees. All tree fecundities must be imputed.

Qui et al. (2023) introduced volatility and period to characterize
and compare masting behavior between trees and species. The tradition
coefficient of variation (CV) ignores the time-dependence in
quasi-periodic seed production. To avoid confusion with indices based on
variance, they introduced the term *volatility* as the
period-weighted spectral density, to allow for the fact that long
intervals are especially important for masting causes and effects on
consumers. In addition to this period-weighting of spectral variance
within a series (a tree), fecundity-weighting is important at the
population scale, because the highly productive individuals dominate
masting effects. Within this framework, *periodicity* extracts
the period (in years) that is likewise weighted to emphasize variance
concentrated at long intervals within trees and fecundity differences
between trees.

The block of code that follows loads output from some trees in the
genus *Abies* from western North America. Specifically, the
estimates for fecundity by tree-year come from the object
`output$prediction$fecPred`

. it uses the function
`mastVolatility`

to compile volatility and periodicity on
each tree and display summaries by ecoregion-species as density plots
and as distributions of mean period estimates.

```
<- function( col, trans ){ # transparent colors
getColor <- col2rgb( col )
tmp rgb( tmp[ 1, ], tmp[ 2, ], tmp[ 3, ], maxColorValue = 255,
alpha = 255*trans, names = paste( col, trans, sep = '_' ) )
}
# from output$prediction$fecPred and output$parameters$betaYrRand
<- "https://github.com/jimclarkatduke/mast/blob/master/outputAbies.rdata?raw=True"
d ::source_data( d )
repmis
<- sort( unique( fecPred$species ) ) # accumulate period estimates
specs <- seq( 0, 10, length = 100 )
yseq <- matrix( 0, length(specs), 100 )
intVal rownames( intVal ) <- specs
<- sort( unique( fecPred$plotSpec ) ) # label trees in a plot-species group
plotSpecs
par( mfrow = c(1, 3), bty = 'n', mar = c(2,4,1,1), omi = c(.5,.1,.1,.1) )
plot( NA, xlim = c(2, 20), ylim = c(.01, 1), xlab = '', ylab = 'Density/nyr', log = 'xy')
for( i in 1:length(plotSpecs) ){
<- which( fecPred$plotSpec == plotSpecs[i] ) # tree-years in group
wi <- fecPred$species[wi[1]]
ci <- match( ci, specs ) # color by species
col
<- mastVolatility( treeID = fecPred$treeID[wi], year = fecPred$year[wi],
tmp fec = fecPred$fecEstMu[wi] )
if( is.null(tmp) )next
<- intVal[ col, ] + dnorm( yseq, tmp$stats['Period', 1], tmp$stats['Period', 2] )
intVal[ col, ]
# density +/- 1 SD
<- tmp$statsDensity
dens lines( dens[ 'Period', ], dens[ 'Mean', ], lwd = 2, col = getColor( col, .4) )
lines( dens[ 'Period', ], dens[ 'Mean', ] - dens[ 'SD', ], lty = 2, col = getColor( col, .4) )
lines( dens[ 'Period', ], dens[ 'Mean', ] + dens[ 'SD', ], lty = 2, col = getColor( col, .4) )
}title( 'a) Plot-species groups' )
legend( 'topright', specs, text.col = c(1:length(specs)), bty = 'n', cex = .8 )
plot( NA, xlim = c(2, 8), ylim = c(0, .12), xlab = '', ylab = 'Density' ) # density of mean intervals
for( i in 1:length(specs) ){
polygon( yseq, intVal[i,]/sum(intVal[i,]), border = i, col = getColor(i, .4) )
}title( 'b) Period estimates' )
```

The following block of code compiles the same densities and summaries
for year effects, which remain after accounting for other predictors in
the model. When fitted with year effects, with
`yearEffect <- list( groups = c( 'species', 'ecoCode' ) )`

,
the column `treeData$ecoCode`

holds the ecoregion where the
tree lives. The `ecoRegion_species`

combinations represent
random groups of year effects that are shared by all trees of the same
species within the same ecoregion. These combinations are
`rownames`

in `output$parameters$betaYrRand`

. Here
I use the function `mastSpectralDensity`

to evaluate
individual rows in `betaYrRand`

.

```
<- strsplit( rownames( betaYrRand ), '_' ) # extract species from ecoregion_species rownames
spec <- sapply( spec, function(x) x[2] )
spec <- sort( unique(spec) )
specs
<- matrix( 0, nrow(betaYrRand), 5 ) # store stats by group
mastMatrix rownames(mastMatrix) <- rownames(betaYrRand)
colnames(mastMatrix) <- c( 'nyr', 'Variance', 'Volatility', 'Period Est', 'Period SD' )
plot( NA, xlim = c(2, 10), ylim = c(.002, .4), xlab = '', ylab = 'Density/yr', log = 'xy')
for(i in 1:nrow(betaYrRand)){
<- which( betaYrRand[i,] != 0 )
wc if( length(wc) < 6 )next
<- mastSpectralDensity( betaYrRand[i,wc] )
s if( !is.matrix( s$spect ) )next
<- c( length(wc), s$totVar, s$volatility, s$periodMu, s$periodSd )
mastMatrix[i, ]
<- 1/s$spec[, 'frequency' ]
period <- s$spec[, 'spectralDensity' ]/length(wc) # series vary in length
dens <- match( spec[i], specs )
col
lines( period, dens, lwd = 2, col = getColor( col, .4) )
}title( 'c) Year effects' )
mtext( 'Period (yr)', 1, line = 1, outer = T )
<- which( is.finite(mastMatrix[,'Variance']) & mastMatrix[,'Variance'] != 0 )
keepRows <- which( colSums( frequency, na.rm=T ) > 0 )
keepCols <- mastMatrix[ keepRows, ] mastMatrix
```

Because seed-trap studies involve multiple data sets ( seed traps,
trees, covariates ) that are collected over a number of years and
multiple sites, combining them can expose inconsistencies that are not
immediately evident. Of course, a proper analysis depends on alignment
of trees, seed traps, and covariates with unique tree names (
`treeData$tree`

) and trap names ( `seedData$trap`

) in each plot ( `treeData$plot, seedData$plot`

).

Notes are displayed by `mastif`

at execution summarizing
aspects of the data that might trigger warnings. All of these issues
have arisen in data sets I have encountered from colleagues:

**Alignment of data frames.** The unique trees in each
plot supplied in `treeData`

must also appear with
`x`

and `y`

in `xytree`

. The unique
traps in each plot supplied in `seedData`

must also appear
with `x`

and `y`

in `xytrap`

. Problems
generate a note:

`Note: treeData includes trees not present in xytree`

**Spatial coordinates.** Because tree censuses and seed
traps are often done at different times, by different people, the grids
often disagree. `Spatial range`

tables are displayed for ( x,
y ) coordinates in `xytree`

and `xytrap`

.

**Unidentified seeds.** Seeds that cannot be identified
to species contain the `character`

string `UNKN`

.
If there are species in `specNames`

that do not appear in
`seedNames`

, then the `UNKN`

seed type must be
included in `seedNames`

and in columns of
`seedData`

. For example, if `caryGlab, caryTome`

appear in `specNames`

, and `caryGlab, caryUNKN`

appear in `seedNames`

( and as columns in
`seedData`

), then `caryUNKN`

will be the imputed
fate for all seeds emanating from `caryOvat`

and some seeds
from `caryGlab`

.

This note will be displayed:

`Note: unknown seed type is caryUNKN`

If there are `seedNames`

that do not appear in
`specNames`

, this note is given:

`Note: seedNames not in specNames and not "UNKN":`

`caryCord`

`Moved caryCord to "UNKN" class`

**Design issues.** The design can seem confusing,
because there are multiple species on multiple plots in multiple years.
There is a design matrix that can be found here for fecundity:

`output$inputs$setupData$xfec`

and here for maturation:

`output$inputs$setupData$xrep`

( Variables are standardized, because fitting is done that way, but
coefficients are reported on their original scales. Unstandardized
versions of design matrices are `xfecU`

and
`xrepU`

. )

There should not be missing values in the columns of
`treeData`

that will be used as predictors ( covariates or
factors ). If there are missing values, a note will be generated:

`Fix missing values in these variables:`

`[1] "yearlyPETO.tmin1, yearlyPETO.tmin2, flowering.covs.pr.data, flowering.covs.tmin.data, s.PETO"`

There can be missing seed counts in `seedData`

–missing
values will be imputed.

A table containing the Variance Inflation Factor ( VIF ), range of
each variable, and correlation matrix will be generated at execution.
VIF values > 10 and high correlations between covariates are taken as
evidence of redundancy. A table will be generated for each species
separately. However, in `xfec`

and `xrep`

they are
treated as a single matrix.

Year effects by random group require replication within groups. Here
is a note for the AR model showing sizes of groups defined by species
and region ( `NE, piedmont, sApps`

):

`no. trees with > plag years, by group:`

```
`caryGlab-NE caryGlab-piedmont caryGlab-sApps `
` 1 497 361 `
`caryOvat-piedmont caryTome-piedmont caryTome-sApps `
` 122 569 77 `
```

`small group: caryGlab-NE`

There is only one tree in the `caryGlab-NE`

group,
suggesting insufficient replication and a different aggregation
scheme.

For the AR( \(p\) ) model, values
are imputed for \(p\) years before and
after a tree is observed, and only trees observed for > \(p\) years will contribute to parameter
estimates. If the study lasts 3 years, then the model should not specify
`yearEffect$p = 5`

. A note will be generated to inform on the
number of observations included in parameter estimates:

`Number of full observations with AR model is: [1] 21235`

**Prediction.** If `predList`

is supplied,
then fecundity and seed density will be predicted for specified
plot-years. The size of the prediction grid is displayed as a table of
prediction nodes by plot and year. Large prediction grids slow
execution. To reduce the size of the grid, increase the
`inputs$predList$mapMeters`

( the default is 5 m by 5 m
).

When covariates are added as columns to `treeData`

, they
must align with `treeData$plot`

, `treeData$year`

,
and, if they are tree-level covariates, with `treeData$tree`

.
The required column `treeData$diam`

is an example of the
latter.

Qiu T., et al., 2022. Limits to reproduction and seed size-number tradeoffs that shape forest dominance and future recovery. Nature Communications, 13:2381 | https://doi.org/10.1038/s41467-022-30037-9

Journe, V., et al., 2022. Globally, tree fecundity exceeds productivity gradients. Ecology Letters, DOI: 10.1111/ele.14012, pdf: Ecology Letters2022.

Sharma, S., et al., 2022. North American tree migration paced by recruitment through contrasting east-west mechanisms. Proceedings of the National Academy of Sciences, 119 (3) e2116691118; https://doi.org/10.1073/pnas.2116691118.

Qiu, T., et al., 2021. Is there tree senescence? The fecundity evidence. Proceedings of the National Academy of Sciences, 118, e2106130118; DOI: 10.1073/pnas.2106130118.

Clark, J.S., 2021. Continent-wide tree fecundity driven by indirect climate effects. Nature Communications DOI: 10.1038/s41467-020-20836-3.

Clark, JS, C Nunes, and B Tomasek. 2019. Masting as an unreliable
resource: spatio-temporal host diversity merged with consumer movement,
storage, and diet. *Ecological Monographs*, 89:e01381.

Clark, JS, S LaDeau, and I Ibanez. 2004. Fecundity of trees and the
colonization-competition hypothesis, *Ecological Monographs*, 74,
415-442.

Clark, JS, M Silman, R Kern, E Macklin, and J Hille Ris Lambers.
1999. Seed dispersal near and far: generalized patterns across temperate
and tropical forests. *Ecology* 80, 1475-1494.

Neal, R.M. 2011. MCMC using Hamiltonian dynamics. In: *Handbook of
Markov Chain Monte Carlo*, edited by S. Brooks, A. Gelman, G. Jones,
and X.-L. Meng. Chapman & Hall / CRC Press.